{"1": {"fulltext": "", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0001.jp2"}, "2": {"fulltext": "", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0002.jp2"}, "3": {"fulltext": "S; A S; ^K\\n*\u00c2\u00a3\u00c2\u00a7y|S Ao* t3\u00c2\u00a7|if* \u00c2\u00abP*\\\\ \u00e2\u0080\u0098illJi^o\\nVk\\nxy V). VTV** A\\nXxx.v A\\nn ^\u00e2\u0080\u0099PX. w v u o ^i-,\\n*\u00c2\u00abfil\u00c2\u00bb X 3 ^V/h, ^Jteter. j$ *jAV/h. i V sjtffok.*\\n*o\\n0y\\nn\\no no\\no% A\\\\*\\nI u\\nX X A\\n%hp/ v\\nl VaaX\\n.0\\nA v V//^^\\\\W t\u00c2\u00bb ^P*. u, jrAnc^\\nv o (r ju 4\\n,V\u00c2\u00b0\u00c2\u00bb i c c f\\nV\\nsw\\n\u00e2\u0080\u009cHis? *^sm?:\\no \u00c2\u00b0o, -p\u00c2\u00b0 J\\nX XV. H a Cv UJ*,\\nvl\\nK *1* o\\nov l *Jii\u00c2\u00a7\\nr\\\\ v\\nO\\nv*.\u00c2\u00abo\u00e2\u0080\u0099*y.. \u00c2\u00b0o,%\\n\u00e2\u0096\u00a0v. V\\nv tt o, 4- \u00e2\u0096\u00a0T\u00e2\u0080\u0099\\nA V o%\u00e2\u0080\u009e\\n\u00c2\u00b0W\u00c2\u00a7iw\u00c2\u00bb ,\u00c2\u00abJ t Wmz j ^v\\n-V Vi. x*\\nV\u00c2\u00b0\\n\u00c2\u00b0o v\\n\u00c2\u00abfe^\\nV \u00c2\u00b0v\\n/-0\\nyjs\u00c2\u00a3$: ~Mik\\nv*c? *QY t\u00c2\u00a7Ksw^,* ^*o*\\nip|ip? 0\\nw 11 V N v^- 1 11\\nKf^ f ^M/)k%\\no ^Oo \u00c2\u00bby 0^\u00e2\u0080\u009d v o ^O-O\\no W l ..V\\ncP\\n-sPV-j v\\nO\u00e2\u0080\u0099\\nK\\n,s \u00e2\u0080\u0098o\\\\^*o,\\\\ fl\\nt\\nr J o vV-^.\\n*+^$Srs\\n%o-\u00e2\u0080\u0098l-v* 4 vC^ *77^ A V\\nC\u00c2\u00b0 NC ^O\\n^\u00e2\u0096\u00a0hcy\\nr ~vr~\\nO\\nP\\na A^\\n5\\nl\u00e2\u0080\u0098.v\\nr A;V.\\n_^ v\\ny o J.^\\nJ\\no *o. ^7Ts a\\n^cPVr^Ao V\\ns^mi\\\\ *of\\np\\ni 6-\\nSWi/v.WA\\nA :4.v X ^X;\\no v,c? ,r\\nX A\\\\ -Aff/ v \u00c2\u00b0\u00c2\u00aex A\\\\\\nO-e^cO-o Ao^ S A\u00c2\u00bb* l **,V\u00c2\u00b0 o^ 0 c 0 A", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0003.jp2"}, "4": {"fulltext": "", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0004.jp2"}, "5": {"fulltext": "United States Office of Air Quality EPA-454/R-00-002\\nEnvironmental Protection Planning and Standards March 2000\\nAgency Research Triangle Park, NC 27711\\nAIR\\nSEPA NATIONAL AIR POLLUTANT\\nEMISSION TRENDS,\\n1900 1998\\nU. S. EPA and the States\\nWorking Together for Cleaner Air!", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0005.jp2"}, "6": {"fulltext": "LC Control Number\\n00 327858\\n2- I 4", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0006.jp2"}, "7": {"fulltext": "NATIONAL AIR POLLUTANT\\nEMISSION TRENDS\\n1900 -1998", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0007.jp2"}, "8": {"fulltext": "Disclaimer\\nTHIS REPORT HAS BEEN REVIEWED BY THE OFFICE OF AIR QUALITY PLANNING AND\\nSTANDARDS. MENTION OF TRADE NAMES OR COMMERCIAL PRODUCTS DOES NOT\\nCONSTITUTE ENDORSEMENT OR RECOMMENDATION FOR USE.\\nL\\n5\\n//^V S 3\\nii Disclaimer", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0008.jp2"}, "9": {"fulltext": "Foreword\\nThis document presents the most recent estimates of national emissions of the criteria air pollutants. The emissions of each\\npollutant are estimated for many different source categories, which collectively account for all anthropogenic emissions. The\\nreport presents the total emissions from all 50 States and from each EPA region in the country. These estimates are updated\\nannually.\\nThis report tracks changes in national emissions since passage of the Clean Air Act Amendments of 1990. The emission\\ntrends are the net effect of many factors, including changes in the nation s economy and in industrial activity, technology,\\nconsumption of fuels, traffic, and other activities that cause air pollution. The trends also reflect changes in emissions as a result\\nof air pollution regulations and emission controls. These reports will serve as a measure of our nation s progress in reducing air\\npollution emissions as a result of mandatory and voluntary controls and of continuous changes in national activity.\\nIn addition to the extensive coverage of criteria air pollutant emissions from anthropogenic sources in the United States, this\\nyear\u00e2\u0080\u0099s report continues to provide limited coverage of State-derived biogenic, greenhouse gas, and air toxic emissions, and\\nemissions for Canada and Europe. Preliminary estimates are presented for the years 1990 through 1998. Final estimates\\n(including refinements to the data used to estimate emissions) will be presented in future reports.\\nForeword iii", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0009.jp2"}, "10": {"fulltext": "[This page intentionally left blank.]", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0010.jp2"}, "11": {"fulltext": "Contents\\nTables.viii\\nFigures..\\nAcronyms and. Abbreviations. xii\\nAcknowledgement.xv\\nExecutive Summary.ES-1\\nES. 1 WHAT INFORMATION IS PRESENTED IN THIS REPORT?.ES-1\\nES.2 WHAT ARE THE CURRENT EMISSION LEVELS? .ES-1\\nES.3 WHAT ARE THE TRENDS IN POLLUTANT EMISSIONS?.ES-1\\nES.4 REFERENCES.ES-2\\n1.0 Introduction .1-1\\n1.1 WHAT INFORMATION IS PRESENTED IN THIS REPORT? .1-1\\n1.2 WHAT ARE THE HEALTH AND ENVIRONMENTAL EFFECTS OF CRITERIA POLLUTANTS?.1-1\\n1.3 WHAT ENHANCEMENTS HAVE BEEN MADE TO THE REPORT?.1-2\\n1.4 HOW IS THE REPORT STRUCTURED?.1-3\\n1.5 REFERENCES .1-5\\n2.0 1998 Emissions .2-1\\n2.1 WHAT EMISSIONS DATA ARE PRESENTED IN THIS CHAPTER?.2-1\\n2.2 HOW HAVE EMISSION ESTIMATES CHANGED FROM 1996 TO 1998 AND WHY?.2-1\\n2.2.1 What Sources Are the Main Contributors to 1998 CO Emissions?.2-1\\n2.2.2 What Sources Are the Main Contributors to 1998 NO x Emissions? .2-2\\n2.2.3 What Sources Are the Main Contributors to 1998 VOC Emissions? .2-2\\n2.2.4 What Sources Are the Main Contributors to 1998 S0 2 Emissions? .2-2\\n2.2.5 What Sources Are the Main Contributors to 1998 Particulate Matter (PM 10 and PM 25 Emissions? 2-3\\n2.2.6 What Sources Are the Main Contributors to 1998 Pb Emissions? .2-3\\n2.2.7 What Sources Are the Main Contributors to 1998 NH 3 Emissions?.2-3\\n2.3 HOW DOES EPA ESTIMATE AND REPORT SPATIAL EMISSIONS? .2-4\\n2.3.1 How Does My State Compare in Rank to Other States?.2-4\\n2.4 WHAT ARE THE LARGEST POINT SOURCES IN THE INVENTORY?.2-4\\n2.5 REFERENCES .2-5\\n3.0 National Emissions Trends, 1900 to 1998 3-1\\n3.1 WHAT DATA ARE PRESENTED IN THIS CHAPTER?.3-1\\n3.2 WHEN DID AIR POLLUTION CONTROL EFFORTS BEGIN AND HOW HAVE THEY EVOLVED? .3-1\\n3.3 WHAT ARE THE GENERAL HISTORICAL EMISSIONS TRENDS?.3-2\\n3.3.1 How Have CO Emissions Changed?.3-2\\n3.3.2 How Have NO x and VOC Emissions Changed?.3-3\\n3.3.3 How Have S0 2 Emissions Changed? .3-3\\nContents v", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0011.jp2"}, "12": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\n3.3.4 How Have PM 10 Emissions Changed?.3-3\\n3.3.5 How Have PM, 5 Emissions Changed? .3-3\\n3.3.6 How Have Pb Emissions Changed? .3-3\\n3.3.7 How Have NH 3 Emissions Changed?.3-3\\n3.4 HOW HAVE EMISSIONS IN THE MAJOR SOURCE CATEGORIES CHANGED ?.3-3\\n3.4.1 How Have Emissions in the Stationary Source Fuel Combustion Categories Changed? .3-4\\n3.4.2 How Have Emissions in the Industrial Process Categories Changed? .3-5\\n3.4.3 How Have Emissions in the On-road Vehicle Categories Changed?.3-6\\n3.4.4 How Have Emissions in the Non-road Engines and Vehicle Categories Changed? .3-7\\n3.4.5 How Have Emissions in the Miscellaneous Categories Changed? 3-8\\n3.5 HOW HAVE EMISSIONS IN THE FUGITIVE DUST CATEGORIES CHANGED?.3-8\\n3.6 REFERENCES .3-8\\n4.0 Section 406 of the Clean Air Act Amendments: Industrial S0 2 Emissions .4-1\\n4.1 WHY A SEPARATE CHAPTER FOR INDUSTRIAL SO, EMISSIONS?.4-1\\n4.1.1 What Source Categories Are Industrial Sources?.4-1\\n4.2 WHY USE 1996 AS THE BASE YEAR?.4-2\\n4.3 HOW DID EPA PROJECT EMISSIONS?.4-3\\n4.4 WHAT IS THE TREND IN INDUSTRIAL SO, EMISSIONS?.4-3\\n4.4.1 Will the Cap Be Exceeded?.4-3\\n4.5 WHAT ARE THE BENEFITS FROM DESULFURIZATION OF DIESEL FUELS?.4-3\\n4.5.1 Why Are Current 1993 Emissions Without Desulfurization Higher Than the Values Presented in the 1995\\nReport to Congress? .4-4\\n4.6 REFERENCES .4-4\\n5.0 National Criteria Pollutant Estimation Methodologies .5-1\\n5.1 WHAT INFORMATION IS PRESENTED IN THIS CHAPTER?.5-1\\n5.2 WHERE DO I GET INFORMATION ON THE METHODS USED TO ESTIMATE EMISSIONS FOR SOURCES\\nWHOSE METHODS DID NOT CHANGE? .5-1\\n5.3 WHAT OTHER THINGS SHOULD I KNOW ABOUT THE TRENDS ESTIMATION METHODS? .5-1\\n5.4 WHAT SOURCE CATEGORIES ARE ESTIMATED USING METHODS THAT DIFFER FROM THE\\nPREVIOUS REPORT? .5-2\\n5.5 HOW WERE EMISSIONS FROM NON-ROAD SOURCES ESTIMATED?.5-2\\n5.5.1 What Types of Sources are Included in the NONROAD Model?.5-2\\n5.5.2 What Years Were Estimated?.5-2\\n5.5.3 Were There Differences in the Methods Used to Calculate Non-road Emissions for Different Years? 5-2\\n5.5.4 Were There Non-road Emission Sources That Were Not Estimated Using the NONROAD Model? 5-3\\n5.5.5 How Were Emissions Estimated for Categories Discussed in Section 5.5.4 Above? .5-3\\n5.5.6 Were Any Pollutant Estimates Prepared Differently for Non-road Sources? .5-4\\n5.6 WHAT CHANGES WERE MADE IN THE METHOD USED TO ESTIMATE NONUTELITY POINT AND\\nAREA SOURCE EMISSIONS?.5-5\\n5.6.1 What Steps Were Required to Incorporate State PEI Data Into the NET? .5-5\\n5.6.2 How Many States Submitted Data for the 1996 PEI Effort?.5-5\\n5.6.3 Were Any State-Supplied Data Rejected in the QC Phase?.5-6\\n5.6.4 What Types of Data Were Augmented in the Data Augmentation Step?.5-6\\n5.6.5 What Quality Assurance Steps Were Taken to Ensure That the State Data Were Incorporated\\nCorrectly? .5-6\\n5.6.6 What Did EPA Do With Comments Received by the States? .5-6\\n5.6.7 Was There Any Additional Data Augmentation? .5-7\\n5.6.8 Were There Emissions From Any Sources Submitted by the States That Were Not Incorporated into the\\nNET?.5-7\\n5.6.9 How Were Nonutility Point and Area Sources for 1997 and 1998 Developed .5-7\\n5.7 WHAT OTHER METHODOLOGY CHANGES WERE THERE?.5-8\\n5.7.1 What Changes Were Made in How Agricultural Livestock Emissions Were Calculated .5-8\\n5.7.2 What Changes Were Made in How Structural Fire Emissions Were Calculated?.5-9\\nvi Contents", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0012.jp2"}, "13": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n5.7.3 What Changes Were Made in How Prescribed Burning Emissions Were Calculated?.5-9\\n5.7.4 How Did EPA Account for Emissions from Heavy-Duty Diesel Engines that Used the NO x Defeat\\nDevice? .5-9\\n5.9 REFERENCES .5-10\\n6.0 Biogenic Emissions .6-1\\n6.1 WHAT EMISSIONS DATA DOES EPA PRESENT IN THIS CHAPTER? .6-1\\n6.2 HOW WERE THESE EMISSIONS GENERATED?.6-1\\n6.3 WHY DO THESE EMISSIONS VARY? .6-1\\n6.4 HOW DOES TEMPERATURE AFFECT EMISSIONS?.6-1\\n6.5 HOW DOES LAND USE AFFECT EMISSIONS? .6-1\\n6.6 WHAT IS THE UNCERTAINTY ASSOCIATED WITH THESE ESTIMATES?.6-1\\n6.7 REFERENCES .6-1\\n7.0 Hazardous Air Pollutants.7-1\\n7.1 WHAT INFORMATION IS PRESENTED IN THIS CHAPTER?.7-1\\n7.2 WHAT ARE THE HEALTH AND ENVIRONMENTAL EFFECTS OF HAPs? .7-1\\n7.3 WHY ARE AIR TOXICS INVENTORIES NEEDED?.7-1\\n7.3.1 Which EPA Regulatory Activities Use HAP Emission Inventories?.7-1\\n7.4 WHAT IS EPA\u00e2\u0080\u0099S PLAN TO GATHER THE NECESSARY TOXICS DATA? .7-2\\n7.5 WHAT IS THE NTI?.7-3\\n7.5.1 How was the NTI Developed?.7-3\\n7.5.2 What are the NTI Base Years?.7-3\\n7.5.3 How are Emissions Allocated to Source Types and Counties?.7-4\\n7.5.4 What are Urban/Rural Allocations? .-.7-4\\n7.5.5 What Changes Have Been Made Since the Last Trends Report? .7-5\\n7.6 HOW ARE THE EMISSIONS SUMMARIZED? .7-5\\n7.6.1 What Individual Pollutant Detail is Given? .7-5\\n7.7 REFERENCES .7-6\\n8.0 National Greenhouse Gas Emissions.8-1\\n8.1 WHAT INFORMATION IS PRESENTED IN THIS CHAPTER?.8-1\\n8.2 WHAT ARE THE RECENT TRENDS IN U.S. GREENHOUSE GAS EMISSIONS?.8-1\\n8.3 WAS A MORE DETAILED ANALYSIS OF INDUSTRIAL EMISSIONS CONDUCTED?.8-2\\n8.3.1 What Data Were Used in this Analysis? .8-2\\n8.3.2 What are the Results? .8-3\\n8.3.3 What Methodologies were Utilized?.8-3\\n8.4 REFERENCES .8-4\\n9.0 International Emissions .9-1\\n9.1 WHAT DATA ARE PRESENTED IN THIS CHAPTER?.9-1\\n9.2 WHAT EUROPEAN EMISSIONS ARE PRESENTED?.9-1\\n9.3 WHAT CANADIAN EMISSIONS ARE PRESENTED?.9-1\\n9.4 REFERENCES .9-2\\nAppendix A National Emissions (1970 to 1998) by Tier 3 Source Category and Pollutant. A-l\\nIndex Index-1\\nContents vii", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0013.jp2"}, "14": {"fulltext": "Tables\\nES-1. 1997 and 1998 National Annual Emission Estimates for Criteria Air Pollutants .ES-3\\nES-2. 1998 National Annual Emission Estimates for PM 25 Ammonia, and 1990-1993 Hazardous Air Pollutants ES-3\\nES-3. Annual Criteria Air Pollutant Emission Estimates for Canada (1995) and Europe (1996) .ES-3\\nES-4. Percentage Change in National Emissions.ES-4\\n1- 1. Major Source Categories.1-6\\n2- 1. 1998 National Point and Area Emissions by Source Category and Pollutant .2-6\\n2- 2. Anthropogenic 1998 State-level Emissions and Rank for CO, NO x VOC, SO,, PM 10 PM 25 and NH 3 .2-8\\n3- 1. Total National Emissions of Carbon Monoxide, 1940 through 1998 3-9\\n3-2. Total National Emissions of Nitrogen Oxides, 1940 through 1998 3-10\\n3-3. Total National Emissions of Volatile Organic Compounds, 1940 through 1998 3-11\\n3-4. Total National Emissions of Sulfur Dioxide, 1940 through 1998 3-12\\n3-5. Total National Emissions of Directly Emitted Particulate Matter (PM 10 1940 through 1998 3-13\\n3-6. Total National Emissions of Directly Emitted Particulate Matter (PM, 5 1990 through 1998 3-14\\n3-7. Total National Emissions of Lead, 1970 through 1998 3-15\\n3-8. Total National Emissions of Ammonia, 1990 through 1998 3-16\\n3-9. Carbon Monoxide Federal Emission Standards, 1970 to 1991 .3-17\\n3-10. Nitrogen Oxide and Volatile Organic Compound Federal Emission Limits for Light-Duty Vehicles, 1972 to 19913-17\\n3-11. Nitrogen Oxide and Volatile Organic Compound Federal Emission Limits for Light-Duty Trucks, 1972 to 1991 3-18\\n3-12. Federal Test Procedure Exhaust Emissions Standards and Schedule for Light-Duty Vehicles and Light-Duty Trucks,\\n1992 to 1998 3-18\\n3- 13. Total National Emissions by Pollutant and Year .3-19\\n4- 1. Industrial S0 2 Tier Source Categories.4-5\\n4-2. Industrial S0 2 Point and Area Data Source Submittals by States .4-6\\n4- 3. Industrial S0 2 Projected Emissions by Selected Source Categories .4-7\\n5- 1. Emission Estimation Methods That Have Changed Since the Last Report.5-11\\n5-2. Point and Area Source Data Submitted.5-12\\n5- 3. Utility Boiler Emissions Data Sources for NO x and SO, by Year .5-14\\n6- 1. Biogenic Volatile Organic Compound Emissions by State .6-2\\n6-2. Biogenic Nitric Oxide Emissions by State.6-3\\n6-3. Biogenic Volatile Organic Compound Seasonal Allocation, 1988 to 1996 6-4\\n6- 4. Biogenic Nitric Oxide Seasonal Allocation, 1988 to 1996 6-4\\n7- 1. Hazardous Air Pollutants Included in the Baseline NTI (version 9901). 7-7\\n7-2. List of Urban HAPS for the Integrated Urban Air Toxics Strategy (\u00e2\u0080\u009cUrban HAPS List\u00e2\u0080\u009d) .7-10\\n7-3. Baseline NTI Emissions for Urban, Rural, and Major Source Categories by HAP.7-11\\n7-4. Baseline NTI (1990 to 1993) 188 HAPS by Urban and Rural Designation and Source Sector (Point, Area, On-road,\\nand Non-road) 7-15\\n7-5. Baseline NTI (1990 to 1993) 188 HAPs by State (Point, Area, On-road, and Non-road).7-23\\n7-6. Baseline NTI (1990 to 1993) 33 HAPs by State (Point, Area, On-road, and Non-road).7-24\\n7-7. Baseline NTI (1990 to 1993) 33 HAPs by Tier 1.7-25\\n7- 8. Baseline NTI (1990 to 1993) 33 HAPs by Tier 1 and Tier 2.7-27\\n8- 1. Recent Trends in U.S. Greenhouse Gas Emissions and Sinks (MMTCE).8-5\\n8-2. Annual Percent Change in CO, Emissions from Fossil Fuel Combustion for Selected Sectors and Fuels.8-6\\n8-3. Carbon Coefficients, MMTCE/QBtu.8-6\\n8- 4. Carbon Dioxide Emissions in the U.S., 1994 (MMTCE) .8-7\\n9- 1. 1996 Emission Estimates for Europe by Country and Pollutant .9-3\\nviii Tables", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0014.jp2"}, "15": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n9-2. 1996 Emission Estimates for Austria and the Czech Republic by CORINAIR/EMEP Source Category and\\nPollutant.9-4\\n9-3. 1996 Emission Estimates for Denmark and Finland by CORINAIR/EMEP Source Category and Pollutant.9-5\\n9-4. 1996 Emission Estimates for France and Germany by CORINAIR/EMEP Source Category and Pollutant.9-6\\n9-5. 1996 Emission Estimates for Greece and Ireland by CORINAIR/EMEP Source Category and Pollutant .9-7\\n9-6. 1996 Emission Estimates for Luxembourg and the Netherlands by CORINAIR/EMEP Source Category and\\nPollutant.9-8\\n9-7. 1996 Emission Estimates for Norway and Slovenia by CORINAIR/EMEP Source Category and Pollutant .9-9\\n9-8. 1996 Emission Estimates for the United Kingdom by CORINAIR/EMEP Source Category and Pollutant.9-10\\n9-9. 1996 Emission Estimates for Austria, Belgium, Czech Republic, and Denmark by EE A Source Category and\\nPollutant.9-11\\n9-10. 1996 Emission Estimates for Estonia, Finland, France, and Germany by EEA Source Category and Pollutant 9-12\\n9-11. 1996 Emission Estimates for Greece, Ireland, Luxembourg, and Netherlands by EEA Source Category and\\nPollutant.9-13\\n9-12. 1996 Emission Estimates for Norway, the Slovenia, Spain, and Sweden by EEA Source Category and Pollutant 9-14\\n9-13. 1996 Emission Estimates for the United Kingdom by EEA Source Category and Pollutant.9-15\\n9-14. 1995 Emissions for Canada by Major Source Category .9-15\\n9-15. 1995 Emissions for Canada by Province.9-15\\nA-l. Carbon Monoxide Emissions. A-2\\nA-2. Nitrogen Oxide Emissions. A-7\\nA-3. Volatile Organic Compound Emissions. A-ll\\nA-4. Sulfur Dioxide Emissions A-19\\nA-5. Directly Emitted Particulate Matter (PM 10 Emissions A-23\\nA-6. Directly Emitted Particulate Matter (PM 2 5 Emissions. A-29\\nA-7. Lead Emissions A-34\\nA-8. Ammonia (NH 3 Emissions. A-37\\nTables ix", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0015.jp2"}, "16": {"fulltext": "Figures\\nES-1. Trend in National Emissions, NITROGEN OXIDES, VOLATILE ORGANIC COMPOUNDS, SULFUR DIOXIDE\\n(1900 to 1998), and Directly Emitted PARTICULATE MATTER (PM 10 [nonfugitive dust sources];\\n1940 to 1998).ES-5\\nES-2. Trend in National Emissions, CARBON MONOXIDE (1940 to 1998), and LEAD (1970 to 1998) .ES-6\\n2-1. 1998 National CARBON MONOXIDE Emissions by Principal Source Categories.2-9\\n2-2. 1998 National NITROGEN OXIDE Emissions by Principal Source Categories .2-10\\n2-3. 1998 National VOLATILE ORGANIC COMPOUND Emissions by Principal Source Categories .2-11\\n2-4. 1998 National SULFUR DIOXIDE Emissions by Principal Source Categories.2-12\\n2-5. 1998 Directly Emitted National PARTICULATE MATTER (PM 10 Emissions by Principal Source Categories for\\nNonfugitive Dust Sources .2-13\\n2-6. 1998 Directly Emitted National PARTICULATE MATTER (PM 25 Emissions by Principal Source Categories for\\nNonfugitive Dust Sources .2-14\\n2-7. 1998 National LEAD Emissions by Principal Source Categories.2-15\\n2-8. 1998 National AMMONIA Emissions by Principal Source Categories .2-16\\n2-9. Density Map of 1998 CARBON MONOXIDE Emissions by County .2-17\\n2-10. Density Map of 1998 NITROGEN OXIDES Emissions by County.2-18\\n2-11. Density Map of 1998 VOLATILE ORGANIC COMPOUND Emissions by County.2-19\\n2-12. Density Map of 1998 SULFUR DIOXIDE Emissions by County.2-20\\n2-13. Density Map of 1998 PARTICULATE MATTER (PM 10 Emissions by County.2-21\\n2-14. Density Map of 1998 PARTICULATE MATTER (PM 2 5 Emissions by County .2-22\\n2- 15. Density Map of 1998 AMMONIA Emissions by County.2-23\\n3- 1. Trend in Gross Domestic Product, Population, Vehicle Miles Traveled, Total Fuel Consumption, Combined\\nVOLATILE ORGANIC COMPOUND and NITROGEN OXIDES Emissions, and SULFUR DIOXIDE Emissions,\\n1970 to 1998 3-21\\n3-2. Trend in CARBON MONOXIDE Emissions, 1940 to 1998 3-22\\n3-3. Trend in NITROGEN OXIDE Emissions, 1940 to 1998 3-23\\n3-4. Trend in VOLATILE ORGANIC COMPOUND Emissions, 1940 to 1998 3-24\\n3-5. Trend in SULFUR DIOXIDE Emissions, 1940 to 1998 3-25\\n3-6. Trend in Directly Emitted PARTICULATE MATTER (PM 10 Emissions Excluding Fugitive Dust Sources, 1940 to\\n1998 3-26\\n3-7. Trend in Directly Emitted PARTICULATE MATTER (PM 25 Emissions Excluding Fugitive Dust Sources, 1990 to\\n1998 3-27\\n3-8. Trend in LEAD Emissions, 1970 to 1998 3-28\\n3- 9. Trend in AMMONIA Emissions, 1990 to 1998 3-29\\n4- 1. S0 2 Emissions by Major Industrial Source Category, 1996 4-8\\n4-2. Industrial S0 2 Emissions (1900 to 2020). 4-9\\n4-3. S0 2 Emissions by Major Industrial Source Category, 2020 4-10\\n4- 4. On-Road Emissions With and Without Desulfurization, 1993-1998 4-11\\n5- 1. States Submitting Point and/or Area Source Data for the 1996 PEI .5-15\\n6- 1. Density Map of NITROGEN OXIDES 1997 Biogenic Emissions by County .6-5\\n6- 2. Density Map of VOLATILE ORGANIC COMPOUND 1997 Biogenic Emissions by County .6-6\\n7- 1. 1996 NTI State Data Summary .7-42\\n7-2. U.S. Counties by Urban and Rural Designation 7-43\\n7-3. Baseline NTI (1990 to 1993) National Emissions by Urban vs. Rural .7-44\\n7-4. Baseline NTI (1990 to 1993) National Emissions of 188 HAPs by Urban vs. Rural .7-45\\nx Figures", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0016.jp2"}, "17": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n7-5. Baseline NTI (1990 to 1993) National Emissions of 33 HAPs by Urban vs. Rural .7-46\\n7-6. Baseline NTI (1990 to 1993) 188 HAP Emissions by State and Source Sector .7-47\\n7-7. Baseline NTI (1990 to 1993) 33 HAP Emissions by State and Source Sector .7-48\\n7-8. Summed Baseline NTI (1990 to 1993) Emissions of 188 HAPs per Square Mile for U.S. Counties .7-49\\n7-9. Summed Baseline NTI (1990 to 1993) Emissions of 33 HAPs per Square Mile for U.S. Counties .7-50\\n7- 10. Summary Baseline NTI (1990 to 1993) of 33 HAPs National Emissions Percentage by Source Sector.7-51\\n8- 1. U.S. Carbon Dioxide Emissions by Sector (1994). 8-8\\n8-2. U.S. Carbon Dioxide Emissions from Industry (1994) 8-9\\n8-3. U.S. Carbon Dioxide Emissions by End-Use Sector (1994) 8-10\\nFigures xi", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0017.jp2"}, "18": {"fulltext": "Acronyms and Abbreviations\\nAIRS\\nAIRS/AFS\\nARD\\nBACT\\nBEA\\nBEIS2\\nBTS\\nBtu\\nCAA\\nCAAA\\nCEM\\nCFCs\\nch 4\\nCHIEF\\nCNG\\nCO\\nC0 2\\nCORINAIR\\nDOE\\nDOT\\nEEA\\nEFIG\\nEGAS\\nEIA\\nEIIP\\nEMEP\\nAerometric Information Retrieval System\\nAIRS Facility Subsystem\\nAcid Rain Division\\nbest available control technology\\nU.S. Department of Commerce, Bureau of Economic Analysis\\nBiogenic Emission Inventory System version 2\\nU.S. DOT, Bureau of Transportation\\nBritish thermal unit\\nClean Air Act\\nClean Air Act Amendments of 1990\\ncontinuous emission monitor(ing)\\nchloroflurocarbons\\nmethane\\nClearinghouse for Inventories and Emission Factors\\ncompressed natural gas\\ncarbon monoxide\\ncarbon dioxide\\nCoordination of Environmental Air\\nDepartment of Energy\\nDepartment of Transportation\\nEuropean Environment Agency\\nEPA, OAQPS, Emission Factor and Inventory Group\\nEconomic Growth Analysis System\\nU.S. DOE, Energy Information Administration\\nEmission Inventory Improvement Program\\nCooperative Programme for Monitoring and Evaluation of the Long Range Transmission of Air\\nPollutants in Europe\\nEPA\\nES\\nETC/AEM\\nETS\\nFAA\\nFIPS\\nFIRE\\nFR\\nFTP\\nGACT\\nGCVTC\\nGDP\\nU.S. Environmental Protection Agency\\nExecutive Summary\\nEuropean Topic Center on Air Emissions\\nEmissions Tracking System\\nFederal Aviation Adminstration\\nFederal Information Processing Standards\\nFactor Information Retrieval\\nFederal Register\\nFederal Test Procedure\\ngenerally achievable control technology\\nGrand Canyon Visibility Transport Commission\\ngross domestic product\\ngPg\\ngP m\\ngrams per gallon\\ngrams per mile\\nxii Acronyms and Abbreviations", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0018.jp2"}, "19": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nGSP\\ngross State product\\nHAPs\\nhazardous air pollutants\\nHCFC\\nhydrochloroflurocarbon\\nHDDV\\nheavy-duty diesel vehicle\\nHDGV\\nheavy-duty gasoline vehicle\\nHFCs\\nhydro flurocarbons\\nID\\nidentification (code)\\nIPCC\\nIntergovernmental Panel on Climate Change\\nLDDT\\nlight-duty diesel truck\\nLDDV\\nlight-duty diesel vehicle\\nLDGT\\nlight-duty gasoline truck\\nLDGV\\nlight-duty gasoline vehicle\\nLDT\\nlight-duty truck\\nLDV\\nlight-duty vehicle\\nLPG\\nliquefied petroleum gas\\nMACT\\nmaximum available control technology\\nMECs\\nManufacturing Consumption of Energy\\nMMTCE\\nmillion metric tons carbon-equivalent\\nMW\\nmegawatts\\nN 2 0\\nnitrous oxide\\nNAA\\nnonattainment area\\nNAAQS\\nNational Ambient Air Quality Standard\\nNADB\\nNational Allowance Data Base\\nNAPAP\\nNational Acid Precipitation Assessment Program\\nNEC\\nnot elsewhere classified\\nNET\\nNational Emissions Trends (inventory)\\nnh 3\\nammonia\\nNMVOC\\nnonmethane volatile organic compounds\\nNO\\nnitric oxide\\nno 2\\nnitrogen dioxide\\nNO x\\nnitrogen oxides\\nNPI\\nNational Particulates Inventory\\nNSPS\\nNew Source Performance Standards\\nNTI\\nNational Toxics Inventory\\n0 3\\nozone\\nOAQPS\\nEPA, Office of Air Quality Planning and Standards\\nOMS\\nEPA, Office of Mobile Sources\\nOTAQ\\nEPA\u00e2\u0080\u0099s Office of Transportation and Air Quality\\nOTAG\\nOzone Transport Assessment Group\\nPb\\nlead\\nPCB\\npolychlorinated biphenyl\\nPEI\\nperiodic emission inventory\\nPFC\\nperfluorocarbon\\nPM\\nparticulate matter\\nPM 10\\nparticulate matter less than 10 microns in diameter\\nPM 2 5\\nparticulate matter less than 2.5 microns in diameter\\nPOM\\npolycyclic organic matter\\nPPm\\nparts per million\\npsi\\npounds per square inch\\nAcronyms and Abbreviations xiii", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0019.jp2"}, "20": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nQA\\nquality assurance\\nQC\\nquality control\\nRACT\\nreasonably available control technology\\nREMI\\nRegional Economic Models, Inc.\\nRFG\\nreformulated gasoline\\nRSD\\nRegulatory Support Document\\nRVP\\nReid vapor pressure\\nsee\\nsource classification code\\nSEDS\\nState Energy Data System\\nsf 6\\nsulfur hexafluoride\\nSIC\\nStandard Industrial Classification (code)\\nSIP\\nState Implementation Plan\\nso 2\\nsulfur dioxide\\nSUV\\nsport utility vehicle\\nTP\\ntotal particulates\\ntpy\\ntons per year\\nTRENDS\\nThe Representative Emissions National Data System\\nTRI\\nToxic Release Inventory\\nTSDF\\nhazardous waste treatment, storage, and disposal facility\\nTSP\\ntotal suspended particulate matter\\nTTN\\nTechnology Transfer Network\\nUNFCCC\\nUnited Nations Framework Convention on Climate Change\\nu.s.\\nUnited States\\nUSDA\\nU.S. Department of Agriculture\\nUSFS\\nUSDA Forest Service\\nVMT\\nvehicle miles traveled\\nVOC\\nvolatile organic compound(s)\\nxiv Acronyms and Abbreviations", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0020.jp2"}, "21": {"fulltext": "Acknowledgement\\nThis report was prepared with the help of many people. The EPA wishes to acknowledge the assistance of the Emission\\nInventory Trends Team of the Emission Factor and Inventory Group, the National Toxics Inventory Team of the Emission Factor\\nand Inventory Group, the Utilities Emissions Representatives of the Clean Air Markets Division; the Nonroad Team of the Office\\nof Transportation and Air Quality; and the Annual Reporting of Green House Gases Report Team of the Climate Policy and\\nPrograms Division; The agency also wishes to acknowledge the data and information that was provided by numerous people\\nfrom Government agencies and private institutions and organizations. This final document was prepared under Contract Number\\n68D-70067.\\nAcknowledgement xv", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0021.jp2"}, "22": {"fulltext": "[This page intentionally left blank.]", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0022.jp2"}, "23": {"fulltext": "Executive Summary\\nES.l WHAT INFORMATION IS\\nPRESENTED IN THIS REPORT?\\nThis report presents the United States (U.S.)\\nEnvironmental Protection Agency\u00e2\u0080\u0099s (EPA) latest estimates of\\nnational emissions for criteria air pollutants: carbon monoxide\\n(CO), nitrogen oxides (NO x volatile organic compounds\\n(VOC), sulfur dioxide (S0 2 particulate matter (PM) less than\\n10 microns in aerodynamic diameter (PM 10 particulate matter\\nless than 2.5 microns in aerodynamic diameter (PM 25 and\\nlead (Pb). In addition, estimates of ammonia (NH 3 an\\nimportant precursor for secondarily formed particles, are also\\npresented. Estimates are presented for the years 1900 to 1998.\\nEstimates for three criteria pollutants, NO x S0 2 and VOC,\\nhave been extrapolated back to 1900. Criteria pollutants are\\nthose for which ambient air standards have been set, based on\\nestablished criteria for risk to human health and/or\\nenvironmental degradation.\\nData on emissions of hazardous air pollutants (HAPs), or\\nair toxics, greenhouse gases (carbon dioxide [C0 2 methane\\n[CHJ, nitrous oxide [N 2 0], hydrofluorocarbons {HFCs],\\nperfluorocarbons (PFCs), and sulfur hexafluoride [SF 6 and\\nbiogenic sources are also included in this report for the United\\nStates. As a point of comparison, data for Canada for 1995\\nand for Europe for 1996 are presented for the criteria air\\npollutants.\\nFigures ES-1 and ES-2 present the long-term trends in the\\ncriteria air pollutant emissions from 1900 through 1998. Most\\nof the criteria air pollutant emission levels peaked around\\n1970. PM 10 emissions peaked earlier (around 1950) since\\nsmoke and particulates were the first pollutants to be\\nregulated. Between 1970 and 1998 emissions for all criteria\\npollutants have generally declined (except for NO x even\\nthough vehicle miles traveled (VMT) and gross domestic\\nproduct (GDP) increased. For the last 2 years, S0 2 has shown\\na small increase in emissions. These air pollution decreases\\nare attributable to the Clean Air Act (CAA) regulations\\nbeginning in 1970 and continuing into the 1990s. (Intermittent\\neconomic recession and improved manufacturing practices\\nhave also played a role.) Although not shown in these figures,\\nthe trend in PM 25 mirrors that of PM, 0 over the period that\\nestimates have been made for PM 25 (1990-1998). NH 3 has\\nshown a modest increase over this same time period.\\nES.2 WHAT ARE THE CURRENT\\nEMISSION LEVELS?\\nTables ES-1 and ES-2 present the most current emission\\nestimates for the criteria and other air pollutants in the United\\nStates. U.S. criteria pollutant emissions decreased for CO,\\nVOC, and NO x and increased for Pb, S0 2 and PM 10 from the\\nprevious year. The increase in SO, emission estimates is a\\nresult of a modest increase in emissions in the electric utility\\nand industrial process sectors, probably fueled by the strong\\neconomy. The reduction in CO and VOC emissions results\\nfrom a sharp decrease in emissions from forest wildfires, as\\nwell as a decrease in mobile source emissions as a result of the\\nuse of new fuels (reformulated gasoline, oxygenated fuels, and\\nlower Reid vapor pressures [RVP]). Particulate fugitive dust\\nemissions from construction sources, paved roads, and\\nunpaved roads increased due to the increases in construction\\nand VMT. The most recent available Canadian data for 1995\\nand Europe for 1996 are summarized in Table ES-3.\\nA description of those source categories whose methods\\nused for estimating CO, NO x VOC, SO,, PM 10 PM 25 NH 3\\nand Pb changed during the last year can be found in Chapter\\n5 of this report, while information on methods that did not\\nchange can be found in the National Air Pollutant Emission\\nTrends Procedures Document. 1\\nES.3 WHAT ARE THE TRENDS IN\\nPOLLUTANT EMISSIONS?\\nThe level and composition of economic activity in the\\nnation, demographic influences, meteorological conditions,\\nand regulatory efforts to control emissions affect the trends in\\ncriteria air pollutant emissions. The emissions resulting from\\nthese economic, demographic, and regulatory influences are\\npresented in Figures ES-1 and ES-2. The changes in\\nemissions are presented in Table ES-4 for several time periods.\\nUp until the 1950s, the greatest influence on emissions were\\neconomic and demographic. Emissions grew as the economy\\nand population increased; emissions declined in periods of\\neconomic recession. Dramatic declines in emissions in the\\n1930s were due to the Great Depression. More recent\\nrecession in the mid/late-1970s (largely a result from\\ndisruptions in the world oil markets) and early 1990s also led\\nto decreases in emissions.\\nEmissions also increase as a result of a shift in the demand\\nfor various products. For example, the tremendous increase in\\nExecutive Summary ES-1", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0023.jp2"}, "24": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\ndemand for refined petroleum products, especially motor\\ngasoline after World War II, increased emissions associated\\nwith petroleum refining and on-road vehicles. Increased\\neconomic production as a result of World War II raised\\nemissions to levels higher than those of the pre-Depression\\nEra. The declines in the 1940s through 1970s in residential\\nwood combustion resulted from the abundant supply, low\\nrelative prices, and convenience of fossil fuel-generated\\nelectricity.\\nIn the 1950s the States issued air pollution statutes\\ngenerally targeted toward smoke and particulate emissions. It\\nwas not until passage of the CAA as amended in 1970\\n(Congress passed the original CAA in 1963) that major strides\\nwere made in reducing air pollution. The 1970 Amendments\\ncreated the EPA and charged it with three major tasks: 1) set\\nNational Ambient Air Quality Standards (NAAQS);\\n2) develop motor vehicle emission standards; and 3) set new\\nsource performance standards (NSPS). As a result of these\\nstandards, CO, VOC, S0 2 and Pb emissions were reduced in\\nthe mid-1970s.\\nThe Clean Air Act Amendments of 1990 (CAAA) are\\nbeginning to effect emission levels. For some source\\ncategories (such as non-road engines), standards began in\\n1996, but some significant emission reductions are not\\nexpected until after the year 2000. The robust U.S. economy\\nin the late 1990s has provided a slight increase in emissions in\\nsome source sectors, although the influence of these increases\\nhas been largely offset by regulatory programs.\\nSome emission sources such as wildfires and fugitive dust\\nhave been influenced more by meteorological conditions than\\neconomic forces. Controls to reduce fugitive dust emissions\\nresulting from the CAAA are beginning to take effect, but are\\nonly applied in the PM nonattainment areas (NAAs). The\\namount of land burned in wildfires varies greatly from\\nyear-to-year. Overall emission reductions from wildfires are\\na result of the U.S. Department of Agriculture\u00e2\u0080\u0099s (USDA)\\nForest Service support of state efforts in fire prevention and\\nearly control. For example, in the year 1910, 5,201 fires\\nburned approximately 5 million acres of land, whereas in the\\nyear 1990, 11,950 fires burned only one-third of a million\\nacres of land.\\nMore details on the effects of economic, demographic,\\nand regulatory forces on emission levels are explained in\\nChapter 3.\\nES.4 REFERENCES\\n1. \u00e2\u0080\u009cNational Air Pollutant Emission Trends Procedures Document, 1900-1996,\u00e2\u0080\u009d EPA-454/R-98-008, U.S. Environmental\\nProtection Agency. May 1998.\\n2. \u00e2\u0080\u009cHistoric Emissions of Sulfur and Nitrogen Oxides in the United States from 1900 to 1980,\u00e2\u0080\u009d EPA-600/7-85-009a and b,\\nU.S. Environmental Protection Agency, Cincinnati, OH. April 1985.\\n3. \u00e2\u0080\u009cHistoric Emissions of Volatile Organic Compounds in the United States from 1900 to 1985,\u00e2\u0080\u009d EPA-600/7-88-008a, U.S.\\nEnvironmental Protection Agency, Cincinnati, OH. May 1988.\\nES-2 Executive Summary", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0024.jp2"}, "25": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable ES-1. 1997 and 1998 National\\nAnnual Emission Estimates for\\nCriteria Air Pollutants\\n(million short tons)\\nEmissions\\nPollutant 1997 1998\\nAnthropogenic Emissions\\nCarbon Monoxide\\n94.41\\n89.45\\nLead (thousand short tons)\\n3.95\\n3.97\\nNitrogen Oxides\\n24.82\\n24.45\\nParticulate Matter (PM 10\\n34.23\\n34.74\\nMiscellaneous and Fugitive\\ndust\\n30.08\\n30.90\\nNonfugitive dust\\n4.15\\n3.84\\nSulfur Dioxide\\n19.62\\n19.65\\nVolatile Organic Compounds\\n18.88\\n17.92\\nBiogenic Emissions\\nVolatile Organic Compounds\\n28.19\\nNA\\nNitric Oxide\\n1.53\\nNA\\nTable ES-2. 1998 National Annual\\nEmission Estimates for PM 25 Ammonia,\\nand 1990-1993 Hazardous Air Pollutants\\n(million short tons)\\nPollutant\\nEmissions\\nParticulate Matter (PM 25\\n8.38\\nMiscellaneous and\\n5.46\\nFugitive dust\\nNonfugitive dust\\n2.92\\nAmmonia\\n4.94\\nHazardous Air Pollutants\\n5.92\\nTable ES-3.\\nAnnual Criteria Air Pollutant Emission\\nfor Canada (1995) and Europe (1996)\\n(million short tons)\\nEstimates\\nPollutant\\nCanada\\nEurope\\nCarbon Monoxide\\n18.89\\n55.53\\nNitrogen Oxides\\n2.72\\n15.31\\nTotal Particulate Matter\\n17.29\\nNA\\nSulfur Dioxide\\n2.93\\n18.53\\nVolatile Organic Compounds\\n3.94\\n16.09\\nExecutive Summary ES-3", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0025.jp2"}, "26": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable ES-4. Percentage Change in National Emissions\\nYear\\nCarbon\\nMonoxide\\nNitrogen\\nOxides\\nVolatile\\nOrganic\\nCompounds\\nSulfur\\nDioxide\\nParticulate\\nMatter\\n(PM in\\nMiscellaneous\\nand\\nFugitive\\nDust**\\nLead\\n1900 to\\n1998\\nNA***\\n-840\\n-111\\n-97\\nNA\\nNA\\nNA\\n1940 to\\n1998\\n5\\n-232\\n-4\\n2\\n76\\nNA\\nNA\\n1970 to\\n1998\\n31\\n-17\\n42\\n37\\n71\\nNA\\n98\\n1988 to\\n1998****\\n25\\n-1\\n26\\n15\\n26\\n45\\n44\\n1990 to\\n1998\\n9\\n-2\\n14\\n17\\n15\\n-26\\n20\\n1997 to\\n1998\\n5\\n2\\n5\\n0\\n7\\n-3\\n-1\\nNote(s):\\nPM, 0 emissions excluding miscellaneous and fugitive dust sources.\\nMiscellaneous sources include agriculture and forestry, fugitive dust includes roads and construction, and natural sources\\ninclude primarily geogenic wind erosion.\\nNA denotes not available. Negative percent change indicates an increase in emissions.\\nThere are significant changes in fugitive dust emission methodology between the years 1989 and 1990.\\nES-4 Executive Summary", "height": "4291", "width": "3099", "jp2-path": "nationalairpollu00unit_0026.jp2"}, "27": {"fulltext": "Figure ES-1. Trend in National Emissions, NITROGEN OXIDES,\\nVOLATILE ORGANIC COMPOUNDS, SULFUR DIOXIDE (1900 to 1998),\\nand Directly Emitted PARTICULATE MATTER\\n(PM 10 [nonfugitive dust sources]; 1940 to 1998)\\nNational Air Pollutant Emission Trends, 1900-1998\\n(SUO} JJOLjS UOjlljUl) SUOjSSjUJg\\nExecutive Summary ES-5\\n1900 1910 1920 1930 1940 1950 1960 1970 1980 1990", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0027.jp2"}, "28": {"fulltext": "Figure ES-2. Trend in National Emissions, CARBON MONOXIDE\\n(1940 to 1998), and LEAD (1970 to 1998)\\nNational Air Pollutant Emission Trends, 1900-1998\\n(suoi ijoijs puesnoip)\\nsuojssjiug pee i\\n(SUO\\\\ IJOljS uonijiu)\\nsuojssiiug 0pjxouo|/\\\\| uoqjeo\\nES-6 Executive Summary\\nYear", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0028.jp2"}, "29": {"fulltext": "Chapter 1.0 Introduction\\n1.1 WHAT INFORMATION IS PRESENTED\\nIN THIS REPORT?\\nThis report presents the United States (U.S.)\\nEnvironmental Protection Agency\u00e2\u0080\u0099s (EPA) latest estimates of\\nnational emissions for criteria air pollutants: carbon monoxide\\n(CO), nitrogen oxides (NO x volatile organic compounds\\n(VOCs [excludes certain nonreactive organic compounds]),\\nsulfur dioxide (S0 2 particulate matter less than 10 microns\\n(PM 10 particulate matter less than 2.5 microns (PM 25 and\\nlead (Pb). Although not a criteria pollutant, emission estimates\\nfor ammonia (NH 3 a compound that plays an important role\\nin the secondary formation of particles, are also presented.\\nThe Clean Air Act (CAA) requires that the EPA Administrator\\npublish a list of pollutants that have adverse effects on public\\nhealth or welfare, and are emitted from numerous and diverse\\nstationary or mobile sources. For each pollutant, the\\nAdministrator must compile and publish a \u00e2\u0080\u009ccriteria\u00e2\u0080\u009d document.\\nThe criteria documents are scientific compendia of the studies\\ndocumenting adverse effects of specific pollutants at various\\nconcentrations in the ambient air. For each pollutant, National\\nAmbient Air Quality Standards (NAAQS) are set at levels\\nthat, based on the criteria, protect the public health and the\\npublic welfare from any known or anticipated adverse effects.\\nThese regulated pollutants are therefore called \u00e2\u0080\u009ccriteria\\npollutants.\u00e2\u0080\u009d We describe some of the health effects in section\\n1 2\\nSummaries of ambient air quality measurements collected\\nby federal, State, and local agencies, and the status of\\ncompliance with the NAAQS, can be found in the series of\\nannual air quality trends reports, the most recent of which is\\nthe National Air Quality and Emissions Trends Report, 1998\\n(EPA-454/R-00-003).\\nGraphs of national emission estimates, beginning in 1900\\nfor NO x VOC, and S0 2 aggregated by major source category,\\nare presented in Chapter 3. We provide more detail for these\\npollutants, and CO and PM 10 beginning with 1940.\\nInformation related to PM 2 5 and NH 3 starts with 1990, the first\\nyear EPA developed estimates for these pollutants. We\\ninclude additional detail for the current year. This report also\\ncontains information on estimation methods that we have\\nupdated during the past year. Revised international emissions\\nfrom Europe and Canada, air toxic emissions, greenhouse gas\\nemissions, and biogenic emissions are also presented.\\n1.2 WHAT ARE THE HEALTH AND\\nENVIRONMENTAL EFFECTS OF\\nCRITERIA POLLUTANTS?\\nCO enters the bloodstream and reduces the delivery of\\noxygen to the body\u00e2\u0080\u0099s organs and tissues. The health threat\\nfrom CO is most serious for those who suffer from\\ncardiovascular disease, particularly those with angina or\\nperipheral vascular disease. It affects healthy individuals also\\nbut only at higher concentration levels. Exposure to elevated\\nCO levels is associated with impairment of visual perception,\\nwork capacity, manual dexterity, learning ability and\\nperformance of complex tasks. 1 Prolonged exposure to high\\nlevels can lead to death.\\nNitric oxide (NO) is the principal oxide of nitrogen\\nproduced in combustion processes; it is readily oxidized in the\\natmosphere to nitrogen dioxide (N0 2 Collectively, NO and\\nN0 2 are referred to as NO x N0 2 can imitate the lungs and\\nlower resistance to respiratory infection (such as influenza).\\nNitrogen oxides are an important precursor both to ozone (0 3\\nand to acidic deposition and may affect both terrestrial and\\naquatic ecosystems. Atmospheric deposition of nitrogen\\n(nitrate, NO x other compounds derived from NOJ leads to\\nexcess nutrient enrichment problems (eutrophication);\\nprominent examples are: Chesapeake Bay and several other\\nnationally important estuaries along the East and Gulf Coasts. 2\\nEutrophication can produce multiple adverse effects on water\\nquality and the aquatic environment, including increased\\nnuisance and toxic algal blooms, excessive phytoplankton\\ngrowth, low or no dissolved oxygen in bottom waters, and\\nreduced sunlight causing losses in submerged aquatic\\nvegetation critical for healthy estuarine ecosystems. Nitrogen\\noxides are a precursor to the formation of nitrate particulate\\nmatter (PM) in the atmosphere; this effect is most important in\\nwestern areas. 3 N0 2 and airborne nitrate also contribute to\\npollutant haze, which impairs visibility and can reduce\\nresidential property values and revenues from tourism.\\nVOCs are a principal component in the chemical and\\nphysical atmospheric reactions that form 0 3 and other\\nphotochemical oxidants. The reactivity of 0 3 causes health\\nproblems because it damages biological tissues and cells. 0 3\\nis also responsible each year for agricultural crop yield loss in\\nthe United States of several billion dollars and causes\\nnoticeable foliar damage in many crops and species of trees.\\nForest and ecosystem studies show that damage is resulting\\n1.0 Introduction 1-1", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0029.jp2"}, "30": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nfrom current ambient 0 3 levels plus excess nutrient enrichment\\nand, in certain high-elevation areas, acidification. 3\\nS0 2 is a precursor to the formation of sulfate PM,\\nincluding acid and nonacid aerosols, in the atmosphere.\\nSulfate aerosols make up the largest single component of fine\\nparticulate matter in most locations in the eastern United\\nStates. 4 The major health effects of concern associated with\\nexposures to high concentrations of SO,, sulfate aerosols, and\\nPM, include effects on breathing, respiratory illness and\\nsymptoms, alterations in the lung\u00e2\u0080\u0099s defenses, aggravation of\\nexisting respiratory and cardiovascular disease, and mortality.\\nChildren and the elderly may be particularly sensitive. Also,\\nSO, can produce foliar damage on trees and agricultural crops.\\nTogether NO x and SO, are the major precursors to acidic\\ndeposition (acid rain), which is associated with several\\nenvironmental and human health effects. These effects include\\nacidification of lakes and streams, impacts on forest soils,\\naccelerated corrosion of buildings and monuments, and\\nvisibility impairment plus respiratory effects on humans\\nassociated with fine sulfate and nitrate particles.\\nBased on studies of human populations exposed to\\nambient particle pollution (sometimes in the presence of S0 2\\nand laboratory studies of animals and humans, the major\\neffects of concern for human health include effects on\\nbreathing and respiratory symptoms, aggravation of existing\\nrespiratory and cardiovascular disease, alterations in the\\nbody\u00e2\u0080\u0099s defense systems against foreign materials, damage to\\nlung tissue, carcinogenesis, and premature mortality.\\nParticulate matter causes damage to materials and soiling; it is\\na major cause of substantial visibility impairment in many\\nparts of the United States. 4\\nFine particles (PM, 5 are of health concern because they\\neasily reach the deepest recesses of the lungs. Batteries of\\nscientific studies have linked fine particles (alone or in\\ncombination with other air pollutants), with a series of\\nsignificant health problems, including:\\nPremature death\\nRespiratory related hospital admissions and\\nemergency room visits\\nAggravated asthma\\nAcute respiratory symptoms, including aggravated\\ncoughing and difficult or painful breathing\\nChronic bronchitis\\nDecreased lung function that can be experienced as\\nshortness of breath\\nWork and school absences 5\\nExposure to Pb can occur through multiple pathways,\\nincluding inhalation of air, diet and ingestion of Pb in food,\\nwater, soil, or dust. Pb accumulates in the body in blood,\\nbone, and soft tissue. Because it is not readily excreted, Pb\\nalso affects the kidneys, liver, nervous system, and blood-\\nforming organs. Excessive exposure to Pb may cause\\nneurological impairments such as seizures, mental retardation\\nand/or behavioral disorders. Even at low doses, Pb exposure\\nis associated with changes in fundamental enzymatic, energy\\ntransfer and homeostatic mechanisms in the body. Fetuses,\\ninfants, and children are especially susceptible to low doses of\\nPb, often suffering central nervous system damage. Recent\\nstudies have also shown that Pb may be a factor in high blood\\npressure and subsequent heart disease in middle-aged\\nCaucasian males. 6\\nNH 3 in the presence of water in the atmosphere reacts\\nwith sulfates and nitrates to create ammonium sulfate and\\nammonium nitrate, both of which are particles. Particles\\nformed via chemical reactions in the atmosphere are known as\\nsecondarily formed particles and play an important role in the\\noverall PM, 5 particle budget.\\n1.3 WHAT ENHANCEMENTS HAVE BEEN\\nMADE TO THE REPORT?\\nSince 1973, EPA has prepared estimates of annual\\nnational emissions in order to assess historic trends in criteria\\npollutant emissions. While these .estimates were prepared\\nusing consistent methodologies and were useful for evaluating\\nemission changes from year to year, they did not provide an\\nabsolute indication of emissions for any given year.\\nBeginning with the 1993 Emission Trends Report (containing\\ndata through 1992), EPA established a goal of preparing\\nemission trends that would also incorporate the best available\\nannual estimates of emissions. a\\nThe EPA\u00e2\u0080\u0099s Emission Factor and Inventory Group (EFIG)\\nhas developed procedures and criteria for replacing Trends\\ndata with emissions data submitted by States as part of a\\nvariety of ongoing programs (such as 0 3 State Implementation\\nPlan [SIP] submitted data). This report contains data obtained\\nfrom several States through the 1996 periodic emission\\ninventory (PEI) data submittals. Information related to how\\nthese data were incorporated into the National Emission\\nTrends (NET) data base is given in Chapter 5.\\nThe EFIG is also developing a data management and\\nreporting system for emissions data. When the system is\\ncomplete, the EFIG can extract the most current State\\ninventories of emissions and supplement the gaps with EPA-\\ngenerated attainment area emission inventories. The EFIG has\\nalready made several changes to the Trends methodology to\\nmake the transition smoother.\\nIn this report, there are five distinct time periods: 1900 to\\n1939, 1940 to 1984, 1985 to 1989, 1990 to 1996, and 1996\\nforward. Since the accuracy and availability of historical data\\nis limited, we have not generally made revisions to estimates\\nbefore 1984 (with some exceptions, discussed in Chapter 5).\\nHowever, many changes in current year totals have been\\nincoiporated into the reported estimates using State data.\\nPlease note that methodologies within a given time\\nperiod (especially more recent periods) will also\\n1-2 1.0 Introduction", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0030.jp2"}, "31": {"fulltext": "vary, as we include more accurate data in the Trends\\ndata base.\\nAlthough there are many changes to the Trends\\nmethodology, some aspects have remained constant. For\\nexample, the 1900 through 1939 NO x VOC, and S0 2\\nestimates are extracted from the National Acid Precipitation\\nAssessment Program (NAPAP) historical emissions report. 7,8\\nIn addition, Pb estimates (1970 to present), and all CO, NO x\\nVOC, SO,, and PM 10 estimates from 1940 to 1984 reported in\\nTrends are based upon the previous national \u00e2\u0080\u009ctop-down\u00e2\u0080\u009d\\nmethodology. Continuous emission monitoring (CEM) data\\nreported by electric utilities to the Acid Rain Program\u00e2\u0080\u0099s\\nEmission Tracking System (ETS) were used, whenever\\navailable and complete, for NO x S0 2 and heat input values\\nfor the years 1996 and 1997. (These data apply to steam\\ngenerated fossil-fuel units with nameplate capacity of at least\\n25 megawatts [MW].) These are some of the most accurate\\ndata collected by EPA because they represent actual\\nmonitored, instead of estimated, emissions. 5\\nAs has been stated in the past several Emission Trends\\nReports, EPA plans to incorporate as much State-derived data\\nas possible into the Trends estimates. This report reflects the\\nuse of State data, specifically those data submitted by various\\nStates as part of the 1996 PEI reporting effort.\\nWhen data were not available, were deemed inappropriate\\nfor use in presenting emission Trends, or when EPA felt that\\nwe had a more robust mechanism for estimating emissions\\nfrom a particular source sector, EPA relied on nationally\\nderived estimates. We describe changes made to estimation\\ntechniques for this year in Chapter 5 of this report. Methods\\nused for other source categories that we did not change for this\\nyear\u00e2\u0080\u0099s report are detailed in the National Air Pollutant\\nEmission Trends, Procedures Document, 1900-1996. 9 In\\ngeneral we updated the 1996 inventory with State data and\\nthen projected estimates for 1997 and 1998 based on economic\\nor other types of growth indicators (such as the State Energy\\nData System (SEDS) fuel consumption estimates) to develop\\nestimates for 1997 and 1998. We also applied reductions\\nresulting from the Clean Air Act Amendments of 1990\\n(CAAA) to the 1997 and 1998 estimates. Throughout the\\nreport we have indicated when the changes in emissions are\\ndue mainly to methodological changes.\\nWe have made two other significant enhancements to the\\nreport. First, the discussions of emission estimates and\\nemission trends are oriented around types of sources rather\\nthan around pollutants. EPA has found that in questions\\nrelated to emissions and emission trends, most requesters want\\ninformation related to how much of a pollutant is emitted by\\na particular source, rather than the total emissions ol a\\npollutant no matter the source. While there are still sections\\nthat discuss overall emissions by pollutant, there are larger\\nsections of the report that we have oriented around the\\nfollowing five categories:\\nNational Air Pollutant Emission Trends, 1900 1998\\ncombustion;\\nindustrial;\\non-road;\\nnon-road; and\\nmiscellaneous.\\nIn particular, these five broader categories are used to\\nprovide additional clarity for information presented\\ngraphically. When these broader categories are used, they\\nrepresent emissions from the following Tier categories (see\\nsection 1.4 and Table 1-1 for Tier category descriptions):\\nCategory\\nTier 1 Categories Included\\nCombustion\\n1,2 and 3\\nIndustrial\\n4, 5, 6, 7, 8, 9, and 10\\nOn-road\\n11\\nNon-road\\n12\\nMiscellaneous\\n13 and 14\\nSome figures also show an \u00e2\u0080\u009call other\u00e2\u0080\u009d category. The all other\\ncategory represents the sum of all other Tier category\\nemissions that are not specifically shown in the figure.\\nThe second major change in the document is the usage of\\n\u00e2\u0080\u009cplain language.\u00e2\u0080\u009d In June 1998, President Clinton issued a\\nmemorandum instructing all government agencies to use plain\\nlanguage in new documents developed after October 1,1998.\\nPlain language is designed to produce documents that have\\nlogical organization, easy-to-read design features, and use\\ncommon, everyday words (except necessary technical terms),\\n\u00e2\u0080\u009cyou\u00e2\u0080\u009d and other pronouns, the active .voice (where possible),\\nand short sentences (where possible). More information about\\nthe plain language initiative can be found at:\\nhttp://www.plainlanguage.gov/\\n1.4 HOW IS THE REPORT STRUCTURED?\\nChanges made in the format of the October 1995 10 report,\\nintended to make the report more comprehensible and\\ninformative, within the framework of the plain language\\ninitiative, are maintained for this report. The executive\\nsummary presents a brief overview of each chapter of the\\nreport. In this introduction, Chapter 1, we inform the reader of\\nchanges to the report, the health effects of criteria air\\npollutants, and the structure of the report. A detailed account\\nof the current year emissions by pollutant, source category.\\nState, nonattainment area (NAA), county, and season and by\\na listing of top-emitting facilities is given in Chapter 2.\\nNational trends in emissions from 1900 (where available) to\\nthe current year and demographic, economic, and regulatory\\ninfluences on emission trends are discussed in Chapter 3.\\nInformation on S0 2 emissions from industrial sources is\\n1.0 Introduction 1-3", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0031.jp2"}, "32": {"fulltext": "National Air Pollutant Emission Trends 1900 1998\\npresented in Chapter 4. An explanation of new methods of\\nestimating pollutant emissions started during the past year is\\nfound in Chapter 5. Biogenic NO x and VOC emissions are\\npresented in Chapter 6. Emissions from sources, noncriteria\\npollutants, or countries not traditionally part of the Trends\\nreport are displayed in Chapters 7, 8, and 9. The EPA and\\nother governmental agencies developed these emissions. In\\neach chapter, numeric superscripts represent references and\\nalphabetic superscripts represent endnotes.\\nAs in last year\u00e2\u0080\u0099s report, all emissions reported in tables\\nand figures in the body of the report are in units of thousand\\nshort tons, except Pb. h The pollutants are presented in the\\norder of CO, NO x VOC, S0 2 PM 10 PM 25 Pb, and NH 3\\nthroughout this report. We developed emissions at the county\\nand Source Classification Code (SCC) level for the years 1985\\nto 1998 for most source categories. We then summed these\\nemissions to the national Tier level. There are four levels in\\nthe tier categorization. The first and second level, respectively\\ncalled Tier 1 and Tier 2, are the same for each of the six\\ncriteria pollutants. [NOTE: Tier 2 in this context should not be\\nconfused with the recently announced Tier II motor vehicle\\ncontrol standards] The third level. Tier 3, is unique for each\\npollutant. The fourth level. Tier 4, is the SCC level. The\\nmatch-up between SCC and all three tier levels can be\\nobtained by contacting EFIG (see Note at the bottom of Table\\n1-1). Table 1-1 lists the Tier 1 and Tier 2 categories used in\\nChapters 1 through 5 to present the criteria air pollutant\\nemission estimates. Tables and figures appear at the end of\\neach chapter in the order in which we have discussed them\\nwithin the chapter. Appendix A contains tables listing\\nemissions for each of the criteria pollutants by Tier 3 source\\ncategories. If emissions are reported as zero, the emissions are\\nless than 0.5 thousand tons (or 0.5 tons for Pb). \u00e2\u0080\u009cNA\u00e2\u0080\u009d\\nindicates that the apportionment of the historic emissions to\\nthese subcategories is not possible. If a tier category does not\\nappear, then emissions are not currently estimated for that\\ncategory (either EPA estimates the emissions as zero or does\\nnot currently estimate the emissions due to time or resource\\nlimitations).\\nThroughout this report, emission estimates of PM 10 and\\nPM 25 are presented by source category as total from all\\nsources, including fugitive dust sources, and nonfugitive dust\\nsources. Fugitive dust sources are included in the following\\ntier categories.\\nTier 1\\nTier 1 Name\\nTier 2 Tier 2 Name\\n13\\nNatural\\nSources\\n02\\nGeogenic (wind erosion)\\n14\\nMiscellaneous\\n01\\nAgriculture and Forestry (agricultural\\ncrops or tilling and feedlots)\\n07\\nFugitive Dust (paved and unpaved\\nroads; unpaved airstrips;\\nconstruction; mining and quarrying;\\nwind erosion industrial; point source\\nhaul roads)\\nEmissions of NO x are expressed as weight-equivalent\\nN0 2 Thus, we have inflated the actual tons of NO emitted to\\nreport them as if they were N0 2 You should therefore assume\\nthat the molecular weight was that of NO, when using\\nnumbers in this report. 0\\nWe report the VOC emissions as the actual weight of\\nmany different compounds. The relative amounts of the\\nindividual compounds emitted will determine the average\\nmolecular weight of a given source category\u00e2\u0080\u0099s emissions.\\nTherefore, no equivalent molecular weight standard exists for\\nVOC. The VOC emissions referred to in this report exclude\\nthose organic compounds considered negligibly\\nphotochemically reactive, according to the EPA definition of\\nVOC in the Code of Federal Regulations (40CFR51.100). 11\\nThus, we have not included methane, ethane, and certain other\\norganic compounds in the VOC totals.\\n1-4 1.0 Introduction", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0032.jp2"}, "33": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n1.5 REFERENCES\\n1. \u00e2\u0080\u009cAir Quality Criteria for Carbon Monoxide,\u00e2\u0080\u009d EPA/600/8-90/045F (NTIS PB93-167492), Office of Health and\\nEnvironment Assessment, Environmental Criteria and Assessment Office, U.S. Environmental Protection Agency,\\nResearch Triangle Park, NC. 1991.\\n2. \u00e2\u0080\u009cAir Quality Criteria for Oxides of Nitrogen,\u00e2\u0080\u009d EPA/600/8-91/049aF-cF.3v, Office of Health and Environment\\nAssessment, Environmental Criteria and Assessment Office, U.S. Environmental Protection Agency, Research Triangle\\nPark, NC. 1993.\\n3. \u00e2\u0080\u009cAir Quality Criteria for Ozone and Other Photochemical Oxidants,\u00e2\u0080\u009d Volume I of III, EPA/600/8-93/004aF, Office of\\nHealth and Environment Assessment, Environmental Criteria and Assessment Office, U.S. Environmental Protection\\nAgency, Research Triangle Park, NC. July 1996.\\n4. \u00e2\u0080\u009cAir Quality Criteria for:Particulate Matter and Sulfur Oxides,\u00e2\u0080\u009d EPA/600/8-82/029aF-cF.3v (NTIS PB84-156777).\\nOffice of Health and Environment Assessment, Environmental Criteria and Assessment Office, U.S. Environmental\\nProtection Agency, Research Triangle Park, NC. 1991.\\n5. \u00e2\u0080\u009cHealth and Environmental Effects of Particulate Matter,\u00e2\u0080\u009d Fact Sheet, Office of Air and Radiation, Office of Air Quality\\nPlanning and Standards, U.S. Environmental Protection Agency, Research Triangle Park, NC. July 17, 1997.\\n6. \u00e2\u0080\u009cAir Quality Criteria for Lead,\u00e2\u0080\u009d EPA/600/8-83/028aF-dF.4v (NTIS PB87-142378), Office of Health and Environment\\nAssessment, Environmental Criteria and Assessment Office, U.S. Environmental Protection Agency, Research Triangle\\nPark, NC. 1991.\\n7. \u00e2\u0080\u009cHistoric Emissions of Sulfur and Nitrogen Oxides in the United States from 1900 to 1980,\u00e2\u0080\u009d EPA-600/7-85-009a and b,\\nU.S. Environmental Protection Agency, Research Triangle Park, NC. April 1985.\\n8. \u00e2\u0080\u009cHistoric Emissions of Volatile Organic Compounds in the United States from 1900 to 1985,\u00e2\u0080\u009d EPA-600/7-88-008a, U.S.\\nEnvironmental Protection Agency, Research Triangle Park, NC. May 1988.\\n9. \u00e2\u0080\u009cNational Air Pollutant Emission Trends Procedures Document, 1900-1996,\u00e2\u0080\u009d EPA-454/R-98-008, U.S. Environmental\\nProtection Agency. May 1998.\\n10. \u00e2\u0080\u009cNational Air Pollutant Emissions Trends, 1900-1994,\u00e2\u0080\u009d EPA-454/R-95-011, Office of Air Quality Planning and\\nStandards, U.S. Environmental Protection Agency, Research Triangle Park, NC. October 1995.\\n11. Code of Federal Regulations Title 40, Volume 2, Parts 50 and 51 (40CFR51.100), pages 131-136, U.S. Government\\nPrinting Office. Revised July 1, 1999.\\na. The great majority of all emission data necessarily are estimates. Exhaustive, on-site quantification, source by source, is a practical, and an\\neconomic, impossibility.\\nb. Lead emissions are measured in short tons. Short tons can be converted to metric tons by dividing the emissions by a factor of 1.1023.\\nc. The term nitrogen oxides (NO x encompasses emissions of both nitrogen dioxide (N0 2 and nitric oxide (NO).\\n1.0 Introduction 1-5", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0033.jp2"}, "34": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 1-1. Major Source Categories\\nTier 1\\nTier 1 Tier 2\\nTier 2\\nTier 1\\nTier 1 Tier 2 Tier 2\\nCODE*\\nNAME CODE\\nNAME\\nCODE\\nNAME CODE NAME\\n01\\nFUEL COMBUSTION-ELECTRIC UTILITIES\\n09\\nSTORAGE TRANSPORT\\n01\\nCoal\\n01 Bulk Terminals Plants\\n02\\nOil\\n02 Petroleum Petroleum Product Storage\\n03\\nGas\\n03 Petroleum Petroleum Product Transport\\n04\\nOther External Combustion\\n04 Service Stations: Stage 1\\n05\\nInternal Combustion\\n05 Service Stations: Stage II\\n02\\nFUEL COMBUSTION-INDUSTRIAL\\n06 Service Stations: Breathing Emptying\\n01\\nCoal\\n07 Organic Chemical Storage\\n02\\nOil\\n08 Organic Chemical Transport\\n03\\nGas\\n09 Inorganic Chemical Storage\\n04\\nOther External Combustion\\n10 Inorganic Chemical Transport\\n05\\nInternal Combustion\\n11 Bulk Materials Storage\\n03\\nFUEL COMBUSTION-OTHER\\n12 Bulk Materials Transport\\n01\\nCommercial Institutional Coal\\n10\\nWASTE DISPOSAL RECYCLING\\n02\\nCommercial Institutional Oil\\n01 Incineration\\n03\\nCommercial Institutional Gas\\n02 Open Burning\\n04\\nMisc. Fuel Combustion (except residential)\\n03 Publicly Owned Treatment Works\\n05\\nResidential Wood\\n04 Industrial Waste Water\\n06\\nResidential Other\\n05 Treatment Storage and Disposal Facility\\n04\\nCHEMICAL ALLIED PRODUCT MFG.\\n06 Landfills\\n01\\nOrganic Chemical Mfg.\\n07 Other\\n02\\nInorganic Chemical Mfg.\\n11\\nON-ROAD VEHICLES\\n03\\nPolymer Resin Mfg.\\n01 Light-Duty Gasoline Vehicles Motorcycles\\n04\\nAgricultural Chemical Mfg.\\n02 Light-Duty Gasoline Trucks\\n05\\nPaint, Varnish, Lacquer, Enamel Mfg.\\n03 Heavy-Duty Gasoline Vehicles\\n06\\nPharmaceutical Mfg.\\n04 Diesels\\n07\\nOther Chemical Mfg.\\n12\\nNON-ROAD ENGINES AND VESSELS\\n05\\nMETALS PROCESSING\\n01 Non-road Gasoline Engines\\n01\\nNonferrous\\n02 Non-road Diesel Engines\\n02\\nFerrous\\n03 Aircraft\\n03\\nMetals Processing (not elsewhere classified\\n04 Marine Vessels\\n[NEC])\\n05 Railroads\\n06\\nPETROLEUM RELATED INDUSTRIES\\n13\\nNATURAL SOURCES\\n01\\nOil Gas Production\\n01 Biogenic\\n02\\nPetroleum Refineries Related Industries\\n02 Geogenic (wind erosion)\\n03\\nAsphalt Manufacturing\\n03 Miscellaneous (lightning/freshwater/saltwater)\\n07\\nOTHER INDUSTRIAL PROCESSES\\n14\\nMISCELLANEOUS\\n01\\nAgriculture, Food, Kindred Products\\n01 Agriculture Forestry\\n02\\nTextiles, Leather, Apparel Products\\n02 Other Combustion (wildfires)\\n03\\nWood, Pulp Paper, Publishing Products\\n03 Catastrophic Accidental Releases\\n04\\nRubber Miscellaneous Plastic Products\\n04 Repair Shops\\n05\\nMineral Products\\n05 Health Services\\n06\\nMachinery Products\\n06 Cooling Towers\\n07\\nElectronic Equipment\\n07 Fugitive Dust\\n08\\nTransportation Equipment\\n09\\nConstruction\\n10\\nMiscellaneous Industrial Processes\\n08\\nSOLVENT UTILIZATION\\n01\\nDegreasing\\n02\\nGraphic Arts\\n03\\nDry Cleaning\\n04\\nSurface Coating\\n05\\nOther Industrial\\n06\\nNonindustrial\\n07\\nSolvent Utilization (NEC)\\nNote(s):\\nCode numbers are presented for The Representative Emissions National Data System (TRENDS) user.\\nThe Source Classification Code (SCC) definitions and assignment to Tier category are available on the Technology Transfer\\nNetwork\u00e2\u0080\u0099s (919-541-5742) Emission Inventories/Emission Factors Information (CHIEF) Technical Information Area, or on the\\nInternet (www.epa.gov/ttn/chief).\\n1-6 1.0 Introduction", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0034.jp2"}, "35": {"fulltext": "Chapter 2.0 1998 Emissions\\n2.1 WHAT EMISSIONS DATA ARE\\nPRESENTED IN THIS CHAPTER?\\nThis chapter describes the carbon monoxide (CO),\\nnitrogen oxides (NO x volatile organic compound (VOC),\\nsulfur dioxide (S0 2 particulate matter less than 10 microns\\n(PM 10 particulate matter less than 2.5 microns (PM 25 lead\\n(Pb), and ammonia (NH 3 emission estimates for 1998. Any\\nnotable trends from 1996 levels are discussed.\\n2.2 HOW HAVE EMISSION ESTIMATES\\nCHANGED FROM 1996 TO 1998 AND\\nWHY?\\nTables A-l through A-7 provide detailed emission\\nsummaries for all pollutants at 5-year intervals from 1970\\nthrough 1985 and yearly for the period 1988 through 1998.\\nExact percentage changes from year to year for specific source\\ncategories can be calculated from those tables. In particular\\nthe tables show that between 1996 and 1998, overall emissions\\nlevels for CO and VOC decreased, NO x remained essentially\\nlevel, while emissions for S0 2 PM 10 and PM 25 and Pb\\nincreased. Specifically,\\n...for utilities\\nS0 2 emissions from point sources increased\\nprimarily due to coal-fired and oil-fired electric\\nutilities. Increased burning of bituminous and\\nanthracite coal by utilities created an increase of\\napproximately 0.5 million tons/year of SOj. 1\\n...for on-road vehicles\\nReductions due to fleet turnover (implementation of\\nTier I standards), 2 reformulated gasoline require\u00c2\u00ac\\nments, oxygenated fuel, and fuels with lower Reid\\nvapor pressure resulted in the decrease in on-road\\nCO, NO x VOC, PM 10 and PM 2 5 emissions despite\\nthe higher vehicle miles traveled (VMT) in 1998.\\nHigher VMT caused an increase in S0 2 and NH 3\\non-road emissions.\\nChanges to 1990-1998 NO x emissions from heavy-\\nduty diesel vehicles (HDDV) due to adjustments in\\nemissions due to the diesel defeat device (see section\\n5.7.4).\\n...for non-road vehicles\\n1998 emissions decreased slightly for CO, NO x and\\nVOC, remained steady for Pb, and increased slightly\\nfor NO x S0 2 PM 10 and PM 25 due to variations in\\nfuel consumption by non-road engines 3 (gasoline and\\ndiesel) and vehicles (airplanes, locomotives, and\\nmarine vessels).\\n...for miscellaneous sources\\n1998 miscellaneous emissions decreased from 1996\\nlevels for all pollutants except PM l0 PM 2 5 and NH 3\\nIncreases in particulate emissions were primarily the\\nresult of increased VMT on paved and unpaved\\nroads, as well as growth in the construction sector\\ndue to the strong economy. Increases in NH 3 were\\nprimarily an inventory artifact resulting from\\nimproved activity data related to agricultural\\nlivestock operations. 4\\n2.2.1 What Sources Are the Main\\nContributors to 1998 CO Emissions?\\nFigure 2-1 is a pie chart showing 1998 CO emissions by\\nsource category. As the figure shows:\\nOn-road vehicles are major contributors to CO\\nemissions, representing 57 percent of total national\\nCO emissions. Of this 57 percent, just over half\\ncomes from light-duty gasoline vehicles (LDGVs\\n[primarily cars]) and motorcycles.\\nNon-road vehicles and engines contribute slightly\\nmore than 20 percent of total CO emissions. These\\nemissions come primarily from gasoline\\nconsumption by lawn and garden, industrial, and\\nrecreational marine engines.\\n2.0 1998 Emissions 2-1", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0035.jp2"}, "36": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nSolvent utilization, storage and transport, and electric\\nutility fuel combustion (three Tier 1 source\\ncategories) contribute slightly more than 0.5 percent\\nto total national CO emissions. These source\\ncategories are combined with petroleum and related\\nindustries, industrial fuel combustion, other industrial\\nprocesses, waste disposal and recycling, and\\nchemical and allied product manufacturing, to create\\nthe \u00e2\u0080\u009call other\u00e2\u0080\u009d grouping in Figure 2-1.\\nTable 2-1 presents the point and area split of the Tier 1\\nsource categories. Area source emissions, including\\ntransportation sources and some minor point sources, comprise\\nover 95 percent of total 1998 CO emissions.\\n2.2.2 What Sources Are the Main\\nContributors to 1998 NO x Emissions?\\nFigure 2-2 is a pie chart showing 1998 NO x emissions by\\nsource category. As the figure shows:\\nOn-road vehicles account for 31 percent of total\\nnational NO x emissions. LDGVs are a major\\ncontributor (approximately 37 percent) to the 1998\\non-road vehicle NO x emissions.\\nElectric utilities represent 25 percent of total national\\nNO x emissions in 1998. Coal combustion represents\\nalmost 90 percent of these emissions, with two-thirds\\nof the coal combustion emissions coming from\\nbituminous coal combustion.\\nSolvent utilization, storage and transport, waste\\ndisposal and recycling, and metals processing (four\\nTier 1 source categories) constitute less that 1 percent\\nof total national NO x emissions. The United States\\n(U.S.) Environmental Protection Agency (EPA)\\nincludes these sources in the \u00e2\u0080\u009call other\u00e2\u0080\u009d grouping in\\nFigure 2-2, along with chemical and allied product\\nmanufacturing, other industrial processes,\\nmiscellaneous, and petroleum and related industries.\\nTable 2-1 presents the point and area split of the Tier 1\\nsource categories. Area source emissions, including\\ntransportation sources, comprise 62 percent of total 1998 NO x\\nemissions. On-road and non-road sources contribute 53\\npercent of the total NO x\\n2.2.3 What Sources Are the Main\\nContributors to 1998 VOC Emissions?\\nFigure 2-3 shows 1998 VOC emissions by source\\ncategory. As the figure indicates:\\nSolvent utilization represents 30 percent of the total\\n1998 VOC emissions. Surface coating constitutes\\njust over 40 percent of the solvent utilization\\nemissions. The 26 specific subcategories of surface\\ncoating estimated by EPA are presented in Table\\nA-3. Table A-3 also shows the effects of control\\nprograms on these sources. For example, co-control\\nof VOCs related to maximum achievable control\\ntechnology (MACT) controls can be seen for 1998\\nemissions from industrial adhesive surface coating\\noperations. A MACT standard for that source\\ncategory went into effect in 1998, reducing emissions\\nby over 50 percent relative to 1996 and 1997 values. 5\\nOn-road vehicles represented 29 percent of total\\nnational VOC emissions. LDGVs account for just\\nover half of total national on-road vehicle VOC\\nemissions.\\nElectric utility fuel combustion and metals\\nprocessing (two Tier 1 source categories) contribute\\nslightly less than 3 percent of total national VOC\\nemissions. EPA combines electric utility fuel\\ncombustion, metals processing, chemical and allied\\nproduct manufacturing, petroleum and related\\nindustries, miscellaneous, other industrial processes\\nand fuel combustion (industrial, other) into an \u00e2\u0080\u009call\\nother\u00e2\u0080\u009d grouping of Figure 2-3. This \u00e2\u0080\u009call other\u00e2\u0080\u009d\\ngrouping contributed 21 percent to the total 1998\\nVOC emissions.\\nTable 2-1 presents the point and area source split of the\\nTier 1 source categories. Area source emissions, including\\ntransportation sources, make up 86 percent of total 1998 VOC\\nemissions.\\n2.2.4 What Sources Are the Main\\nContributors to 1998 SO, Emissions?\\nFigure 2-4 is a pie chart showing 1998 S0 2 emissions by\\nsource category. As the figure shows:\\nElectric utilities contribute the majority of SO,\\nemissions, representing over two-thirds (68 percent)\\nof total national S0 2 emissions in 1998. Well over\\n90 percent of these emissions come from coal\\ncombustion. Bituminous coal combustion accounts\\nthree-fourths of the electric utility coal combustion\\nemissions.\\nIndustrial coal combustion produced 15 percent of\\nthe 1998 SO, emissions.\\nSolvent utilization, storage and transport, waste\\ndisposal and recycling, on-road sources, and\\n2-2 2.0 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0036.jp2"}, "37": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nmiscellaneous (five Tier 1 source categories) account\\nfor 2 percent of total national SO, emissions. These\\nsources, along with non-road sources, petroleum and\\nrelated industries, and other industrial processes,\\ncomprise EPA\u00e2\u0080\u0099s \u00e2\u0080\u009call other\u00e2\u0080\u009d grouping.\\nTable 2-1 presents the point and area split of the Tier 1\\nsource categories. Area source emissions, including\\ntransportation sources, make up 14 percent of total 1998 SO,\\nemissions, while point sources make up the remainder.\\n2.2.5 What Sources Are the Main\\nContributors to 1998 Particulate Matter\\n(PM 10 and PM 2 5 Emissions?\\nFigures 2-5 and 2-6 are pie charts showing 1998 PM 10\\nand PM, 5 emissions by source category. They depict the\\nnonfugitive dust sources of PM 10 and PM, 5 As the figures\\nshow:\\nFuel combustion processes (utilities, industrial,\\ncommercial, and institutional boilers, and area source\\ncombustion) contribute the most to the nonfugitive\\ndust portions of PM. Mobile sources, both on-road\\nand non-road, are the next largest category of\\nemitters. Industrial processes collectively comprise\\nonly about 10 percent of the nonfugitive dust sources,\\nbut they could have a significant effect on air quality\\nin their vicinity.\\nWildfire PM 10 and PM 25 emissions for 1998\\ndecreased significantly relative to 1996 and 1997\\nlevels due to a dramatic reduction in the number of\\nacres burned. Managed burning and wildfires\\ncomprise most of the area source combustion\\ncontributions in Figures 2-5 and 2-6.\\nAlthough the NET inventory shows that fugitive dust\\ncontributes a large percentage to the total PM emissions, a\\nreport by the Desert Research Institute found that about 75%\\nof these emissions are within 2 m of the ground at the point\\nthey are measured. Thus, most of them are likely to be\\nremoved or deposited within a few km of their release,\\ndepending on atmospheric turbulence, temperature, soil\\nmoisture, availability of horizontal and vertical surfaces tor\\nimpaction and initial suspension energy. This is consistent\\nwith the generally small amount of crustal materials found on\\nspeciated ambient samples. 6\\nFor a complete understanding of PM, 5 emissions, one\\nshould also consider the emissions of SO,, NO x and NH V\\nThese gases react in the atmosphere to form ammonium sulfate\\nand ammonium nitrate fine particles; also, some organic\\nparticles are formed from VOCs. These \u00e2\u0080\u009csecondary\u00e2\u0080\u009d tine\\nparticles (in contrast to the directly emitted particles from\\ncombustion and fugitive dust) can comprise as much as half\\nthe PM 2 5 measured in the U.S. 7 Source apportionment studies\\nexist to help elucidate the role of primary PM (reflected in the\\nNET) and secondary PM.\\nTable 2-1 presents the point and area split of the Tier 1\\nsource categories. Area source emissions, including\\ntransportation sources, make up 96 percent of total 1998 PM 10\\nemissions. Methods and related data sources for several area\\nsource categories are currently being reviewed. These include\\nunpaved roads, open burning, and construction.\\nNote that some emission estimates have not been updated.\\nFor example, wind erosion particulate emissions have been\\nmaintained at a constant value since 1996. Also, annual\\nestimates of wind erosion emissions are difficult to interpret,\\nowing to the extremely short duration of most wind events.\\n2.2.6 What Sources Are the Main\\nContributors to 1998 Pb Emissions?\\nFigure 2-7 is a pie chart showing 1998 Pb emissions by\\nsource category. As the figure shows:\\nMetals processing contributes 53 percent to total\\nnational Pb emissions. Nonferrous metal processing\\nrepresents 65 percent of the 1998 metals processing\\nemissions. Primary and secondary Pb products\\nrepresent 46 and 37 percent, respectively, of the\\nnonferrous metals in 1998.\\nOn-road emissions account for less than 0.5 percent\\nof total national Pb emissions.\\nEPA does not estimate Pb emissions for the\\nfollowing 5 Tier 1 source categories because Pb\\nemissions from these sources are thought to be\\nnegligible: solvent utilization, storage and transport,\\npetroleum and related industries, natural sources, and\\nmiscellaneous. Figure 2-7 shows the percentage\\ncontribution from the remaining 9 Tier 1 categories.\\nThe \u00e2\u0080\u009call other\u00e2\u0080\u009d grouping includes chemical and allied\\nproduct manufacturing, other industrial processes,\\nand fuel combustion (electric utility and industrial).\\n2.2.7 What Sources Are the Main\\nContributors to 1998 NH 3 Emissions?\\nFigure 2-8 is a pie chart showing 1998 NH 3 emissions by\\nsource category. As the figure shows, livestock agriculture\\ncontributes the largest amount of NH 3 emissions. Livestock\\nagriculture and fertilizer application combined comprise 86\\npercent of total national NH 3 emissions in 1998. Currently,\\nthe USDA and EPA are working to refine the NH 3 inventory\\nfor all source categories, including some natural and biogenic\\ncategories that are not in the current inventory. As mentioned\\nabove (section 2.2.5), NH 3 is involved in the formation of\\n2.0 1998 Emissions 2-3", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0037.jp2"}, "38": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nammonium sulfate and ammonium nitrate particles. The NH 3\\ninventory is important to perform modeling simulations to\\nunderstand the formation of these particles in the atmosphere\\nusing transport and transformation models.\\n2.3 HOW DOES EPA ESTIMATE AND\\nREPORT SPATIAL EMISSIONS?\\nEPA estimates emissions at the county level and then\\nsums them to the state level for all criteria pollutants except Pb\\nand for all source categories except fugitive dust sources and\\nwildfires (whose emissions are estimated at the State level and\\nare allocated to the county level using spatial surrogates).\\nFigures 2-9 through 2-15 present the broad geographic\\ndistributions of 1998 emissions based on each county\u00e2\u0080\u0099s\\ntonnage per square mile. Specifically,\\nFigure 2-9 shows that (on an emission density basis)\\nthe eastern third of the United States and the west\\ncoast emit more CO than the western two-thirds of\\nthe continental United States.\\nFigures 2-10 through 2-12 show that the eastern half\\nof the United States and the west coast emit more\\nNO x VOC, and S0 2 than the western half of the\\ncontinental United States.\\nFugitive dust emissions, which predominate in rural\\nand agricultural areas, comprise the major component\\nof PM 10 and PM, 5 emissions. NH 3 emissions follow\\na similar pattern, although they are primarily\\nassociated with agricultural and fertilizer sources\\nrather than fugitive dust.\\n2.3.1 How Does My State Compare in Rank\\nto Other States?\\nTo understand how a particular State ranks relative to\\nmagnitude of emissions, refer to Table 2-2, which presents the\\ntotal state-level emissions and state rankings for all pollutants.\\nEPA summed the county-level emissions to produce\\nthe state-level emissions.\\nThe estimates for Alaska and Hawaii include only\\non-road vehicle, point source, residential wood\\ncombustion, and wildfire emissions. PM I0 and PM, 5\\nestimates also include some fugitive dust estimates\\nfor Alaska and Hawaii. (A base year inventory\\nsimilar to National Acid Precipitation Assessment\\nProgram (NAPAP) was not available for these\\nstates.)\\n2.4 WHAT ARE THE LARGEST POINT\\nSOURCES IN THE INVENTORY?\\nRefer to Table 2-1 to understand which categories contain\\nthe largest amount of point sources. Historically, steel mills,\\nsmelters, utility plants, and petroleum refining produce the\\nlargest point source emissions. We usually provide point\\nsource top 50 lists in this report; however, this year new\\nperiodic emission inventory (PEI) point source data was\\nreceived and was still being quality assured at press time.\\nOnce the State data is deemed accurate, EPA intends to post\\ntop 50 lists by pollutant on EPA\u00e2\u0080\u0099s Emission Factor and\\nInventory Group\u00e2\u0080\u0099s (EFIG) web site (expected later in 2000).\\nThe internet address for the EFIG is:\\nhttp://vvww.epa.gov/ttn/chief/efig.\\n2-4 2.0 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0038.jp2"}, "39": {"fulltext": "National Air Pollutant Emission Trends 1900 1998\\n2.5 REFERENCES\\n1. http://www.epa.gov/acidrain/cems/cemlng.html\\n2. Federal Register as 56 FR 25724, June 5, 1991.\\n3. http://www.epa.gov/otaq/nonrdmdl.htm\\n4. 1997 Census of Agriculture: Geographic Area Series, Volume 1, 1 A, IB, 1C [machine-readable data file] United States\\nDept, of Agriculture, National Agricultural Statistics Service. Washington, D.C.: The Service [producer and distributor],\\n1999.\\n5. Listing of MACT rules may be found at: http://www.epa.gov/ttn/uatw/eparules.html\\n6. Watson, John G. and Judith C. Chow, \u00e2\u0080\u009cReconciling Urban Fugitive Dust Emissions Inventory and Ambient Source\\nContribution Estimates: Summary of Current Knowledge and Recent Research\u00e2\u0080\u009d DRAFT, Desert Research Institute\\nDocument No. 61104dD2, Reno, NV, September 3, 1999. (This document may be found at:\\nhttp//www.epa.gov/ttn/chief/ap42pdf/fugitive.pdf)\\n7. \u00e2\u0080\u009cNational Air Quality and Emission Trends Report, 1997\u00e2\u0080\u009d, EPA-454/R-98-016, Office of Air Quality Planning and\\nStandards, U.S. Environmental Protection Agency, Research Triangle Park, NC. Pages 42-45, December 1998.\\n8. \u00e2\u0080\u009cNational Air Pollutant Emissions Trends, 1900-1996,\u00e2\u0080\u009d EPA-454/R-97-011, Office of Air Quality Planning and\\nStandards, U.S. Environmental Protection Agency, Research Triangle Park, NC. December 1997.\\n9. Bollman, A.D. and G. Stella, \u00e2\u0080\u009cStatus and Future Plans for the Economic Growth Analysis System (EGAS).\u00e2\u0080\u009d Proceedings\\nof the Air Waste Management Association Emission Inventory Specialty Conference, New Orleans, LA, December 8-\\n10, 1998.\\n2.0 1998 Emissions 2-5", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0039.jp2"}, "40": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n2-6 2.0 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0040.jp2"}, "41": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n2.0 1998 Emissions\\n2-7", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0041.jp2"}, "42": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 2-2. Anthropogenic 1998 State-level Emissions and Rank for\\nCO, NO x VOC, S0 2 PM 10 PM 25 and NH 3\\n(thousand short tons)\\nState\\nRank\\nO\\nO\\nRank\\nNO x\\nRank\\nVOC!\\nRank\\nS0 2\\nRank\\nPM, 0\\nRank\\nPM 2\\nRank\\nnh 3\\nAlabama\\n12\\n2,3611\\n15\\n619\\n16\\n419!\\n9\\n764!\\n19\\n619\\n15\\n184\\n24\\n88\\nAlaska\\n13\\n2,249!\\n44\\n99\\n14\\n457!\\n50\\n12!\\n39\\n274\\n19\\n155\\n51\\n1\\nArizona\\n27\\n1,370:\\n23\\n450\\n26\\n281!\\n26\\n225!\\n36\\n336\\n24\\n145\\n36\\n35\\nArkansas\\n31\\n1,1471\\n35\\n267\\n32\\n223!\\n36\\n125!\\n23\\n529\\n25\\n132\\n10\\n161\\nCalifornia\\n1\\n8,072!\\n2\\n1,456\\n2\\n1,215}\\n28\\n1821\\n3\\n1,973\\n3\\n535\\n7\\n211\\nColorado\\n29\\n1,200l\\n25\\n400\\n27\\n274!\\n35\\n137!\\n24\\n518\\n29\\n126\\n15\\n111\\nConnecticut\\n37\\n793 i\\n41\\n153\\n35\\n156!\\n41\\n66!\\n45\\n119\\n45\\n30\\n45\\n8\\nDC\\n51\\niooi\\n51\\n23\\n51\\n22!\\n51\\n11!\\n51\\n6\\n51\\n2\\n50\\n2\\nDelaware\\n50\\n216:\\n47\\n77\\n48\\n51!\\n37\\n96!\\n48\\n39\\n48\\n14\\n43\\n12\\nFlorida\\n3\\n5,203:\\n5\\n1,059\\n3\\n891!\\n6\\n1,008!\\n11\\n822\\n7\\n260\\n22\\n94\\nGeorgia\\n4\\n3,998!\\n12\\n730\\n9\\n576!\\n13\\n660!\\n7\\n1,103\\n4\\n320\\n17\\n106\\nHawaii\\n47\\n3211\\n48\\n59\\n47\\n53!\\n47\\n35!\\n49\\n35\\n49\\n11\\n47\\n7\\nIdaho\\n34\\n956!\\n43\\n116\\n39\\n115!\\n46\\n39!\\n14\\n678\\n17\\n161\\n27\\n78\\nIllinois\\n9\\n2,890!\\n4\\n1,076\\n6\\n748!\\n4\\n1,153!\\n9\\n1,028\\n6\\n261\\n11\\n148\\nIndiana\\n11\\n2,526!\\n7\\n848\\n12\\n518!\\n3\\n1,164!\\n17\\n641\\n20\\n154\\n18\\n104\\nIowa\\n33\\n1,0451\\n30\\n343\\n31\\n239!\\n23\\n283!\\n20\\n602\\n27\\n130\\n2\\n305\\nKansas\\n28\\n1,230!\\n20\\n479\\n30\\n257!\\n30\\n163!\\n4\\n1,570\\n5\\n299\\n4\\n232\\nKentucky\\n26\\n1,3891\\n14\\n682\\n23\\n330!\\n10\\n753!\\n35\\n345\\n35\\n103\\n21\\n95\\nLouisiana\\n14\\n2,184:\\n9\\n825\\n15\\n425!\\n16\\n405!\\n27\\n441\\n23\\n149\\n13\\n130\\nMaine\\n42\\n488!\\n45\\n94\\n40\\n109!\\n44\\n53!\\n42\\n158\\n36\\n102\\n46\\n8\\nMaryland\\n32\\n1,1071\\n29\\n344\\n33\\n183!\\n19\\n339!\\n41\\n227\\n42\\n57\\n38\\n28\\nMassachusetts\\n30\\n1,1 88!\\n31\\n304\\n29\\n264!\\n24\\n264!\\n38\\n290\\n40\\n72\\n42\\n14\\nMichigan\\n7\\n3,309!\\n6\\n880\\n4\\n765!\\n14\\n628!\\n21\\n569\\n21\\n153\\n29\\n70\\nMinnesota\\n22\\n1,552:\\n21\\n476\\n19\\n381!\\n31\\n162!\\n10\\n1,011\\n10\\n222\\n8\\n198\\nMississippi\\n25\\n1,414!\\n28\\n353\\n24\\n304!\\n21\\n305!\\n26\\n458\\n26\\n130\\n23\\n91\\nMissouri\\n19\\n1,816!\\n16\\n546\\n20\\n360!\\n15\\n482!\\n5\\n1,286\\n8\\n252\\n6\\n221\\nMontana\\n39\\n703!\\n39\\n176\\n42\\n105!\\n42\\n60!\\n6\\n1,137\\n12\\n216\\n19\\n96\\nNebraska\\n40\\n681!\\n36\\n239\\n36\\n154!\\n38\\n94!\\n18\\n632\\n30\\n125\\n3\\n241\\nNevada\\n41\\n520!\\n40\\n157\\n43\\n98!\\n40\\n66!\\n44\\n143\\n44\\n39\\n40\\n17\\nNew Hampshire\\n45\\n355!\\n46\\n82\\n45\\n74!\\n34\\n148!\\n47\\n54\\n47\\n17\\n48\\n3\\nNew Jersey\\n24\\n1,454!\\n22\\n466\\n17\\n408!\\n25\\n257!\\n37\\n313\\n37\\n96\\n41\\n15\\nNew Mexico\\n36\\n855!\\n32\\n279\\n38\\n140!\\n27\\n199!\\n1\\n4,987\\n1\\n781\\n34\\n49\\nNew York\\n6\\n3,337}\\n13\\n723\\n5\\n753!\\n12\\n688!\\n12\\n767\\n11\\n222\\n30\\n69\\nNorth Carolina\\n10\\n2,773!\\n11\\n745\\n8\\n605!\\n11\\n729!\\n25\\n501\\n16\\n172\\n9\\n183\\nNorth Dakota\\n43\\n380!\\n37\\n235\\n41\\n105!\\n20\\n327!\\n29\\n430\\n38\\n92\\n26\\n79\\nOhio\\n5\\n3,934!\\n3\\n1,198\\n7\\n706!\\n1\\n1,921}\\n16\\n658\\n13\\n195\\n16\\n111\\nOklahoma\\n23\\n1,518!\\n24\\n440\\n25\\n295!\\n32\\n157!\\n8\\n1,033\\n14\\n193\\n5\\n222\\nOregon\\n18\\n1,988!\\n33\\n271\\n28\\n272!\\n43\\n58!\\n13\\n686\\n9\\n224\\n31\\n65\\nPennsylvania\\n8\\n2,909!\\n8\\n840\\n10\\n575!\\n2\\n1,221}\\n22\\n547\\n18\\n156\\n20\\n96\\nRhode Island\\n49\\n221!\\n50\\n35\\n49\\n49!\\n49\\n12!\\n50\\n25\\n50\\n8\\n49\\n2\\nSouth Carolina\\n20\\n1,638!\\n26\\n367\\n22\\n334!\\n22\\n290!\\n30\\n410\\n34\\n112\\n37\\n33\\nSouth Dakota\\n46\\n333!\\n42\\n119\\n44\\n78!\\n45\\n53!\\n34\\n349\\n39\\n73\\n12\\n132\\nTennessee\\n16\\n2,037!\\n10\\n761\\n11\\n528!\\n7\\n789!\\n33\\n375\\n28\\n130\\n25\\n83\\nTexas\\n2\\n5,644!\\n1\\n2,140\\n1\\n1,388!\\n5\\n1,096!\\n2\\n3,655\\n2\\n733\\n1\\n511\\nUtah\\n35\\n942!\\n38\\n233\\n34\\n161!\\n39\\n79!\\n40\\n238\\n41\\n69\\n35\\n36\\nVermont\\n48\\n240!\\n49\\n46\\n50\\n44!\\n48\\n16!\\n46\\n75\\n46\\n18\\n44\\n10\\nVirginia\\n15\\n2,149!\\n17\\n532\\n13\\n471!\\n18\\n373!\\n31\\n409\\n32\\n118\\n28\\n73\\nWashington\\n17\\n2,035!\\n27\\n364\\n21\\n347!\\n33\\n155!\\n28\\n430\\n22\\n149\\n32\\n59\\nWest Virginia\\n38\\n721\\n18\\n500\\n37\\n141\\n8\\n787!\\n43\\n152\\n43\\n50\\n39\\n19\\nWisconsin\\n21\\n1,600!\\n19\\n480\\n18\\n400!\\n17\\n378!\\n32\\n391\\n33\\n112\\n14\\n124\\nWyoming\\n44\\n361!\\n34\\n270\\n46\\n68!\\n29\\n179!\\n15\\n663\\n31\\n122\\n33\\n53\\nNational\\n89,454!\\n24,454\\n17,917!\\n19,647!\\n34,741\\n8,379\\n4,935\\nNote(s): The sums of States may not equal National totals due to rounding.\\n2-8 2.0 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0042.jp2"}, "43": {"fulltext": "Figure 2-1. 1998 National CARBON MONOXIDE Emissions\\nby Principal Source Categories\\nW\\nc\\nCO\\n\u00e2\u0096\u00a0D\\n(0\\no\\noc\\nc\\nO\\nO)\\nc\\no\\nLU\\nx:\\nXJ\\n0)\\n(0\\no\\ncc\\n1\\n\u00e2\u0096\u00a0O\\nc\\nc\\n0\\no\\n1998 Emissions 2-9\\nMetals Processing", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0043.jp2"}, "44": {"fulltext": "National Air Pollutant Emission Trends 1900-1998\\nc\\no\\n0)\\nE\\nLU\\nLU\\ns\\nD\\nX 5\\no o\\nU)\\nz o\\nHi 03\\n(D o\\nO d)\\nDC o\\nt 3\\nz o\\n0)\\nCO _\\nc 0\\no a\\n(0\\no\\n00 Q.\\nO)\\nJr\\nc\\\\i\\nCVJ\\n1\\nU)\\nmwmm\\nLL\\nc\\no\\nc\\no\\nT5\\nC\\n0\\nT\\n0\\nO\\nDC\\nI\\nc\\no\\nD\\nC\\nO)\\nc\\nLU\\nT3\\n(D\\nO\\nDC\\nc\\no\\nz\\na\\no\\n(D\\nTJ\\nC\\nCO\\n2-10 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0044.jp2"}, "45": {"fulltext": "Figure 2-3. 1998 National VOLATILE ORGANIC COMPOUND Emissions\\nby Principal Source Categories\\nNational Air Pollutant Emission Trends, 1900-1998\\nZ\\n1998 Emissions 2-11", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0045.jp2"}, "46": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\no\\nE\\nLU\\nLU\\no\\nX\\no\\nQ\\n0C\\nLL\\n0\\no\\n00\\no\\nO)\\n(0\\nD\\nmmm\\no\\nO)\\n0\\n0\\no\\n0\\no\\no\\n0\\nQ.\\nO\\nc\\nI\\nCM\\n0\\n3\\nO)\\nLL\\nc\\no\\nC/\\n3\\n4-\u00c2\u00bb\\nD\\n22\\n(0\\no\\no\\na_\\no\\nO\\n0)\\nd)\\n3\\nLU\\nLL\\n2-12 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0046.jp2"}, "47": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\ni\\nc\\no\\nTJ\\nC\\n(0\\nTD\\n0\\nO\\ncc\\nc\\no\\no\\nC/)\\n0\\nO\\nU)\\n0\\ncs\\no\\n0\\no\\nLU 9\\nro\\ni\u00e2\u0080\u0094\\n(0\\ntt 0\\n3\\no o\\n0 .Or\\nT3\\nC\\nO\\nk.\\nQ .E\\n0)\\nJZ\\noo\\nO\\no\\nin\\nCM\\n0\\nn\\nc\\no\\n(0\\n0)\\n1\\n6\\n3\\nTD TD\\nc c\\nCC\\n03\\n1 g\\nE\\n3\\n\u00e2\u0080\u0098c\\nO\\nE\\nE\\n03 CO\\nC\\nE o\\no tz\\no Q_\\n03\\nTD\\nC\\no\\no\\nD\\nCO\\nTD\\nc\\n03\\nLU\\nCL\\n03\\nE\\no O\\n03\\nCD CO\\n03\\nCO\\nD c\\nO\\nO)\\ncd\\nco\\nCD CO\\nJZ CD\\nH O\\nn\\n-S 03\\nX Q.\\n(1)\\n-O C\\nc\\nX\\n03\\n8\\nO D\\no CD\\nw 0\\nCO m\\nS|E\\nCO\\nCO\\nE O\\nCl) o\\nCD\\nJZ r-\\nD\\nTD\\n0\\nc\\no\\no\\no\\nJO\\nCD\\n32\\n3\\nO\\nJZ\\n(0\\n0)\\nc\\no\\n(1)\\nk\u00e2\u0080\u0094\\n03\\n(0\\no\\ng\\ntz\\n03\\nQ.\\nO\\nm\\nE?\\n05 O\\n2 B\\nE E\\nCD O\\ni/j CO\\nif w\\n03\\nO co\\nO) Cl)\\ng o\\ntd tz\\n5 CD\\n03 Q.\\ne cd\\ncd .g\\nO\\nC CD\\nO\\n0)\\nO\\nk_\\n1)\\nQ)\\n03\\n\u00e2\u0080\u00a2g\\n(J\\n_3\\nQ)\\nQ.\\nD\\nJZ\\no\\nTo\\nX\\nD\\n(0\\nQ)\\nTD\\n3\\n00\\nc\\n0)\\nE\\nc\\no\\ntz\\no\\no.\\nCL\\n03\\nCD\\no\\nk_\\n3\\nO\\nw\\nrig\\nS\u00e2\u0080\u0099 a,\\n03 JZ\\nC\\nQ) TD\\n.tZ CD\\nC TD\\n3\\n11\\nc O\\nS\u00e2\u0080\u0099 2\\n3\\n0 CO\\nCD CD\\nCD O\\nE 3\\n2\\nCL 3\\n0)\\nJZ a)\\nO)\\n3\\nE\\no\\nk_\\n0\\nc\\no\\n0)\\nCL\\nE\\no\\no\\n(D\\nw_\\no\\nLO\u00c2\u00ac\\nCO\\n03 0\\n0\\n5 E\\nL\\nE\\no\\no\\nc\\n(0 o\\no z\\n35\\nTD CL\\n1998 Emissions 2-13", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0047.jp2"}, "48": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nCO\\nc\\no\\nE\\nLU\\n0)\\nwmm\\no\\nU)\\n0)\\nCO\\nO\\na)\\na\\n3\\nO\\nCO\\nQ.\\nmmm\\no\\nQ\\nCO\\nO)\\nO)\\nCD\\ni\\nCM\\nCD\\nC/)\\nO\\n\u00e2\u0080\u009835\\nc/\\ng,E\\n:r LU\\n.2\\ni\\nC\\no\\nTJ\\nC\\n(0\\nT5\\n(0\\nO\\noc\\nI\\nc\\nO\\nO\\nc\\ncc\\nw\\nG)\\nc\\nD)\\nC\\nLU\\nTJ\\n0\\nO\\nOC\\nW\\no\\no\\nJC\\na\\ni D\\nC\\nCD o\\n=3 O\\n0\\n-O O CO\\nC C\\n03 0\\na\\n~o\\nc\\nC 03\\nTO C\\nLU\\no\\nw j=) 2\\nill\\np\\nE o -o\\nEi i)\\naJ 0\\nc\\nE\\no -c\\nO Q. 2\\n0) N\\n0\\nc r\\nQ. c E\\nD -c\\nO Q.\\no o\\n0 D m\\nD\\nr T3 O\\n(1)\\nC _c\\na)\\no\\n03\\np co _0\\n03\\nCO\\n0\\nCO\\n03\\nO)\\n0\\nCO\\nQ) 0\\nJZ 0\\nh- g\\n\u00e2\u0080\u0099n\\n_P 0\\n\u00e2\u0096\u00a0g\\no\\no\\n0\\nQ.\\n0\\n.c\\no\\n0\\nX\\nX Q. 0\\nCO\\nX3\\nD\\nO\\n0\\n0 Q\\n\u00c2\u00a7;E\\nCO\\nE O\\nO\\nE\\n2\\nco D\\nC\\no E\\no t\\no 5\\n0\\n-O\\n1 8\\n5 P\\n0 t\\n0 2\\nc c\\no c\\nS S\\nO\\nco C\\na\\nc\\n0\\nE\\nc\\no\\ntr\\no\\nCL\\na.\\n0\\n0\\nE\\nD\\nO\\nc n s\\n15\\n0 TD\\n0\\nC TD\\nD\\nI\\no\\nc\\nO\\nf CO\\n0\\nO\\n0 C\\n0\\nCO CO\\n0 0\\n0 O\\nE 3\\n3 8\\n5\\nCL D\\nO\\n0\\nCO 0\\nw CO\\nO 13\\nc o\\n\u00e2\u0096\u00a0o tr\\n5 \u00c2\u00ab3\\n0 Q_\\nS 0\\n0 .E\\nTD\\nI\\n0\\nQ.\\nE\\nCD\\nD\\ni\\nO\\nCO\\nc\\nCO O\\n0 0\\n0\\nE\\n0\\no\\nLL\\n0\\nCO\\n\u00e2\u0096\u00a00\\nCL\\nE 0\\n8\\nc S\\n0 O\\nO Z\\n\u00c2\u00a75\\n\u00e2\u0096\u00a0O CL\\n2-14 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0048.jp2"}, "49": {"fulltext": "Figure 2-7. 1998 National LEAD Emissions\\nby Principal Source Categories\\nNational Air Pollutant Emission Trends, 1900-1998\\nCO\\nO)\\nCO\\nc\\no\\nQ.\\no\\nCO\\no\\nQ\\nCD\\nCD\\ncc\\nCO\\n\u00e2\u0096\u00a0D\\nco\\nC\\nCO\\nCO\\n0\\no\\n0\\nd\\n4-*\\nTJ\\nO\\nC\\nCO\\nU)\\nc\\nCO\\nCO\\nCD\\no\\no\\nl\u00e2\u0080\u0094\\nCL\\nCO\\nCO\\nCD\\n1998 Emissions 2-15", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0049.jp2"}, "50": {"fulltext": "National Air Pollutant Emission Trends 1900-1998\\n0)\\no\\nU)\\no\\ncs\\no\\n1\\no\\n3\\nO\\n0\\nCL\\nmmm\\no\\n00\\nI\\nCVI\\no\\n3\\nOl\\nLL.\\nn\\nCO\\n3\\nO\\nCO\\nD d\\nC D\\n(0 3\\n0)\\nO\\n0\\nO\\nc\\nD\\nC\\n(0\\no\\no\\nCO\\nCD\\no\\nN\\na\\noS\\nto\\n(0\\nU)\\no\\nc\\na\\nCO\\no\\nN\\nQ\\no\\no\\nCD\\nOC\\nCO\\n03\\n2-16 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0050.jp2"}, "51": {"fulltext": "Figure 2-9. Density Map of 1998 CARBON MONOXIDE\\nEmissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\n2.0 1998 Emissions 2-17", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0051.jp2"}, "52": {"fulltext": "Figure 2-10. Density Map of 1998 NITROGEN OXIDE\\nEmissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\n2-18 2.0 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0052.jp2"}, "53": {"fulltext": "Figure 2-11. Density Map of 1998 VOLATILE ORGANIC COMPOUND\\nEmissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\n2.0 1998 Emissions 2-19", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0053.jp2"}, "54": {"fulltext": "Figure 2-12. Density Map of 1998 SULFUR DIOXIDE\\nEmissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\n2-20 2.0 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0054.jp2"}, "55": {"fulltext": "Figure 2-13. Density Map of 1998 PARTICULATE MATTER (PM 10\\nEmissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\n2.0 1998 Emissions 2-21", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0055.jp2"}, "56": {"fulltext": "Figure 2-14. Density Map of 1998 PARTICULATE MATTER (PM 2 .s)\\nEmissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\n2-22 2.0 1998 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0056.jp2"}, "57": {"fulltext": "Figure 2-15. Density Map of 1998 AMMONIA Emissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\n2.0 1998 Emissions 2-23", "height": "4291", "width": "3146", "jp2-path": "nationalairpollu00unit_0057.jp2"}, "58": {"fulltext": "[This page intentionally left blank.]", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0058.jp2"}, "59": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nChapter 3.0 National Emissions Trends,\\n1900 to 1998\\n3.1 WHAT DATA ARE PRESENTED IN\\nTHIS CHAPTER?\\nThis chapter presents historical trends in air pollutant\\nemissions [carbon monoxide (CO), nitrogen oxides (NO x\\nvolatile organic compounds (VOCs), sulfur dioxide (S0 2\\nparticulate matter less than 10 microns (PM 10 particulate\\nmatter less than 2.5 microns (PM 2 5 and lead (Pb). Although\\nnot a criteria pollutant, emission estimates for ammonia (NH 3\\nfor the period 1900 through 1998 (where available). The\\nsource categories discussed in this chapter include: fuel\\ncombustion, industrial processes (chemical and allied\\nproducts, metals processing, petroleum and related industries,\\nother industrial processes, solvent utilization, storage and\\ntransport, and waste disposal and recycling), on-road vehicles,\\nnon-road engines and vehicles, and miscellaneous. This\\nchapter also describes the effects that national economic\\nactivity and regulatory efforts have had on air pollutant\\nemissions trends.\\nIn this chapter, values representing changing emissions or\\nthe percentage change in emissions over various time periods\\nare presented. It is important for the reader to realize that all\\nvalues are estimates only and possess a large degree of\\nuncertainty. Uncertainty analyses are ongoing at the United\\nStates (U.S.) Environmental Protection Agency (EPA) and\\nwill be reported in the FY2001 report.\\n3.2 WHEN DID AIR POLLUTION\\nCONTROL EFFORTS BEGIN AND HOW\\nHAVE THEY EVOLVED?\\nIn 1881, the cities of Chicago and Cincinnati, in an effort\\nto control smoke and soot primarily from furnaces and\\nlocomotives, passed the first air pollution statutes in the\\nUnited States. By the early 1900s, county governments began\\nto pass their own pollution control laws. In 1952, Oregon\\nbecame the first state to legislatively control air pollution, and\\nother states soon followed, enacting air pollution statutes\\ngenerally aimed at controlling smoke and particulates.\\nThe Federal Government became involved in air pollution\\ncontrol in 1955 with the passage of the Air Pollution Control\\nAct. This law limited Federal involvement in air pollution\\ncontrol to providing funding assistance for the States air\\npollution research and training efforts. The shift by the\\nFederal Government toward greater involvement in air\\npollution control began with the passage of the original Clean\\nAir Act (CA A) in 1963. This act provided permanent Federal\\nsupport for air pollution research, continued and increased\\nFederal assistance to states for developing their air pollution\\ncontrol agencies, and a mechanism through which the Federal\\nGovernment could assist states with cross-boundary air\\npollution problems. In^ 965, Congress amended the CAA for\\nthe first time, directing the Secretary of Health, Education, and\\nWelfare to set the first Federal emissions standards for motor\\nvehicles.\\nIn 1967, Congress passed the Air Quality Act, which\\nrequired that states establish air quality control regions and\\nthat Health, Education, and Welfare, through the National Air\\nPollution Control Administration, conduct research on the\\neffects of air pollution, operate a monitoring network, and\\npromulgate criteria to serve as the basis for setting emission\\nstandards. States would then use the HEW information to set\\nair quality standards. In addition, the Air Quality Act directed\\nHEW to identify control technologies for states to use to attain\\nthe air quality standards that each state was to have\\nestablished.\\nSeveral problems undermined this early period of federal\\nair pollution control. The HEW belatedly issued guidance\\ndocuments detailing the adverse health effects associated with\\ncommon air pollutants; where guidance documents had been\\nprepared, states either failed to set air quality standards or\\nfailed to develop implementation plans in a timely manner. In\\naddition, the initial exhaust emission standards set by HEW in\\n1968 resulted only in relatively small reductions in automobile\\npollutants.\\n1970 marked the beginning of several major changes to\\nfederal air pollution control efforts. First, the Federal\\nGovernment created a new federal agency, the EPA, on\\nDecember 2, 1970, and charged it with the responsibility of\\nsetting National Ambient Air Quality Standards (NAAQS).\\nSecond, EPA was given the authority to develop national\\n3.0 Summary of National Emissions Trends 3-1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0059.jp2"}, "60": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nemissions standards for cars, trucks, and buses. Finally,\\nCongress gave EPA the power to set emissions performance\\nstandards [known as new source performance standards\\n(NSPS)] for all new sources of the common air pollutants.\\nUnder the CAA, the only major responsibility that states\\nretained was that of determining how to control existing\\nsources.\\nIn response to its mandate, the EPA promulgated primary\\nand secondary NAAQS in 1971 for photochemical oxidants,\\nS0 2 total suspended particulate (TSP), CO, and hydrocarbons.\\nTo comply with each of the NAAQS by a 1975 deadline, states\\nhad to develop and implement State Implementation Plans\\n(SIPs) that would demonstrate how existing sources would be\\ncontrolled. In 1977, Congress made additional modifications\\nto the CAA, laying the groundwork for more significant\\nchanges to occur with the passage of the CAA Amendments\\n(CAAA).\\nThe photochemical oxidants standard formulated by EPA\\nin 1971 set an hourly average level that was not to be exceeded\\nmore than once per year. In 1979, EPA changed the chemical\\ndesignation of the NAAQS from photochemical oxidants to\\nozone (0 3 In 1979, EPA revised the 0 3 standard from 0.08\\nparts per million (ppm) of 0 3 to 0.12 ppm of 0 3 measured over\\na 1-hour period, not to be exceeded more than three times in a\\n3-year period. In July 1997, EPA once again revised the 0 3\\nstandard, returning it to 0.08 ppm of 0 3 but measured over an\\n8-hour period, where a formal exceedance was triggered by the\\nfourth highest concentration over a 3-year period. The District\\nof Columbia Circuit Court remanded this revision in May of\\n1999, placing the status of the new 8-hour 0 3 NAAQS in\\nquestion.\\nThe regulatory discussion in this report is not\\ncomprehensive; instead, it emphasizes some of the regulatory\\nefforts that have targeted the major source categories for each\\nair pollutant. An example is the national Acid Rain Program\\nauthorized by Title IV of the 1990 CAAA. The initial phase\\nof its innovative market-based S0 2 reduction program began\\nin 1995 and, during the first year of compliance, utilities cut\\nSO, emissions from their Phase I (Table A) units by\\napproximately 40 percent. Phase I of the Acid Rain NO x\\nreduction program, a more conventional rate-based control\\nprogram for coal-fired utility boilers, began in 1996 and\\ncontributed to the general decline in NO x emissions in the late\\n1990s.\\nHowever, the lack of detail available for all of the data\\nprecludes the possibility of analyzing some of the stationary\\nsource control measures [for example, state-specific\\nregulations such as reasonably available control technology\\n(RACT) provisions]. As a point of reference. Figure 3-1\\npresents the trends in gross domestic product (GDP),\\npopulation, vehicle miles traveled (VMT), and total fuel\\nconsumption (that is, total fuel consumed by industrial,\\nresidential, commercial, and transportation sectors) from 1970\\nto 1998.\\nIn the fall of 1998, EPA issued a new regulation requiring\\n22 states and the District of Columbia to submit SIPs to\\ndiminish the regional transport of ground-level 0 3 through\\nreductions in NO x This regulation is commonly known as the\\nNO x SIP call. By reducing NO x emissions, this rule aims to\\nreduce the transport of ground-level ozone across state\\nboundaries in the eastern half of the United States. The rule\\nrequires NO x emission reduction measures to be in place by\\nMay 1, 2003. While EPA does not mandate which sources\\nmust reduce pollution, EPA expects utilities and large\\nnon-utility point sources to be the most likely sources of NO x\\nemissions reductions. The rule also establishes a NO x Budget\\nTrading Program which should enable states to achieve over\\n90 percent of the required emissions reductions in a highly\\ncost-effective manner. EPA projects that full implementation\\nof the NO x SIP call would reduce NO x emissions in the eastern\\nUnited States by 25 percent, or approximately 1.142 million\\ntons, beginning in the year 2003. Timing is uncertain due to\\nlitigation.\\n3.3 WHAT ARE THE GENERAL\\nHISTORICAL EMISSIONS TRENDS?\\nTables 3-1 through 3-8 present emissions trends for the\\nperiod 1940 through 1998 for CO, NO x VOC, S0 2 PM 10\\nPM 25 Pb, and NH 3 Appendix Tables A-l through A-7\\npresent detailed emissions for the years 1970 through 1998,\\n\u00e2\u0080\u009cwhere available.\u00e2\u0080\u009d CO, VOC, S0 2 and Pb emissions peaked\\nin or around 1970, with a general downward trend during the\\n1970 to 1998 time frame. PM 10 emission levels peaked around\\n1950, steadily declined until the mid-1980s, and since then\\nhave remained relatively stable. NO x emissions steadily\\nincreased through the mid-1970s to 24.4 million tons in 1980,\\ndeclined slightly during the early 1980s, and then climbed\\nagain, exceeding 25 million tons in 1994. Total NO x\\nemissions have since declined slightly. From 1990 to 1998,\\nNH 3 emissions rose by 14 percent, while PM 25 emissions\\nremained relatively stable. Figures 3-2 through 3-9 depict\\nemission estimates for each source category from 1940 to\\n1998 (where available).\\n3.3.1 How Have CO Emissions Changed?\\nTable 3.1 shows historical trends in CO emissions by\\nprincipal source categories. Total CO emissions peaked in\\n1970 and decreased rather steadily thereafter. A significant\\ndecrease in CO emissions occurred between 1973 and 1975 as\\na result of disruptions in world oil markets and a subsequent\\nrecession in the United States. (NO x and VOC emissions\\ntrends also showed similar short-term decreases from 1973 to\\n1975 for the same reasons.) The fluctuations of CO emissions\\nin the late 1980s is due to the variation in wildfire activity\\nfrom year-to-year.\\n3-2 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0060.jp2"}, "61": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n3.3.2 How Have NO x and VOC Emissions\\nChanged?\\nThis report often considers NO x and VOC together\\nbecause they comprise the principal components in the\\nchemical and physical atmospheric reactions that form 0 3 and\\nother photochemical oxidants. Although an ambient air\\nquality standard does not exist for VOC, VOC emissions are\\nan important category from the standpoint of modeling 0 3\\nformation.\\nWith regard to NO x total national emissions increased\\n233 percent between 1940 and 1998. Changes in emissions\\nover this time period are shown in Table 3-2. From 1970 to\\n1997, NO x emissions increased by approximately 19 percent,\\nfollowed by a slight decline in 1998.\\nTable 3-3 presents the trend in VOC emissions from 1940\\nthrough 1998. Total national VOC emissions rose\\nsignificantly from 1940 to 1970, but then declined almost as\\nsignificantly from 1970 to 1998. In fact, 1998 levels exceed\\n1940 VOC emission levels by less than one million tons.\\nWhen calculating VOC emissions, EPA includes those\\nemissions of VOC species that primarily contribute to the\\nformation of 0 3 in total VOC emissions but excludes\\nemissions of methane (CH 4 a nonreactive compound. EPA\\nmakes no adjustments to include chlorofluorocarbons (CFCs)\\nor to exclude ethane and other VOCs with negligible\\nphotochemical reactivity, and it estimates on-road vehicle\\nemissions as nonmethane hydrocarbons. Chapter 6 discusses\\nemissions of organic compounds from biogenic sources such\\nas trees and other vegetation. According to recent research,\\nnatural sources emit almost the same level of VOC emissions\\nas anthropogenic sources, but the extent to which biogenic\\nVOC emissions contribute to oxidant formation has not been\\ndetermined.\\n3.3.3 How Have SO, Emissions Changed?\\nTable 3-4 presents the trend in SO, emissions between\\n1940 and 1998. National SO, emissions rose 56 percent from\\n1940 to 1970 and have since declined, primarily because of\\nregulatory actions, especially those that targeted utility\\nsources.\\n3.3.4 How Have PM 10 Emissions Changed?\\nTable 3-5 presents the 1940 to 1998 trend in PM 10\\nemissions. EPA divides PM 10 sources into two categories:\\nfugitive dust sources and nonfugitive dust sources. PM 10\\nfugitive dust sources include natural sources (geogenic wind\\nerosion) and some miscellaneous sources. These\\nmiscellaneous sources include agriculture and forestry fugitive\\ndust sources. The PM 10 nonfugitive dust sources include all\\nother PM 10 sources. For 1998, EPA estimates that total\\nnational fugitive dust PM 10 emissions are approximately 8\\ntimes greater than total emissions from nonfugitive dust\\nsources. Since 1990, emissions from fugitive dust sources\\nhave increased slightly, primarily as the result of increases in\\nunpaved road and construction emissions.\\n3.3.5 How Have PM 25 Emissions Changed?\\nThis most recent Trends report includes data on PM 25\\nemission trends since 1990. EPA originally developed\\nemissions estimates for PM 2 5 under the National Particulate\\nInventory (NPI). This study consisted of a 1990 air emissions\\ninventory for the United States (excluding Alaska and\\nHawaii), Canada, and Mexico. For the 1998 Trends report,\\nEPA uses State particulate data where available to develop\\nPM 25 estimates. As can be seen in Table 3-6, overall PM 25\\nemissions remain relatively constant from 1990to 1998, while\\nemissions from residential wood combustion decline\\nsignificantly and emissions from natural sources fluctuate.\\n3.3.6 How Have Pb Emissions Changed?\\nTable 3-7 provides data on Pb emissions from 1970\\nthrough 1998. The promulgation of a national ambient air\\nquality standard for Pb in October 1978 has been the primary\\nforce behind the dramatic decrease in Pb emissions from\\n220,869 tons in 1970 to 3,973 tons in 1998.\\n3.3.7 How Have NH 3 Emissions Changed?\\nThis Trends report also includes data on NH 3 emission\\ntrends since 1990. Table 3-8 presents the emissions data for\\nNH 3 since 1990. Fuel combustion-industrial, on-road\\nvehicles, and miscellaneous sources saw the greatest growth\\nin emissions during the 1990s, while chemical and allied\\nproduct manufacturing and petroleum and related industries\\nsaw the greatest declines in emissions during that same period.\\n3.4 HOW HAVE EMISSIONS IN THE\\nMAJOR SOURCE CATEGORIES\\nCHANGED?\\nThis section discusses the trends in emissions from a\\nsource category perspective rather than a pollutant perspective.\\nWhile each pollutant is discussed relative to the source\\ncategory being considered, the main emphasis is on the\\nchanges that have occurred in that source category. In\\naddition, this section occasionally discusses long term trends\\nin emissions. As a point of reference. Table 3-13 presents\\ntotal national (but not source category specific) emission\\nestimates for each pollutant for each year available from 1900\\nto 1998.\\n3.0 Summary of National Emissions Trends 3-3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0061.jp2"}, "62": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n3.4.1 How Have Emissions in the Stationary\\nSource Fuel Combustion Categories\\nChanged?\\nThe three stationary source fuel combustion categories are\\nfuel combustion electric utility, fuel combustion industrial,\\nand fuel combustion other. Fuel combustion other includes\\ncommercial/institutional coal, commercial/institutional oil,\\ncommercial/institutional gas, miscellaneous fuel combustion\\n(except residential), residential wood and residential other.\\nFigures 3-2 through 3-9, present trends in CO, NO x VOC,\\nPM, PM, 5 Pb, and NH 3 emissions from fuel combustion\\nsources from as early as 1940 in most cases, to 1998.\\nEmissions of SO, from fuel combustion sources peaked\\nin 1973, declined sharply in the mid 1990s, but are rising\\nagain. NO x emissions from fuel combustion sources peaked\\na few years later, in 1977, and remained approximately\\nconstant at their peak level through the mid 1990s.\\nMeanwhile, VOC and PM 10 emissions declined steadily from\\n1940 until the early 1970s. Emissions then rose, but declined\\nagain in the late 1980s. Pb emissions peaked in 1972 and have\\nsince declined significantly. Although overall CO emissions\\ndeclined steadily from 1940 until 1970, they reversed trend\\nafter 1970, peaking at 8 million tons in 1985. PM 25 emissions\\nhave declined overall between 1990 and 1998. While NH 3\\nemissions from fuel combustion sources rose slightly since\\n1990, fuel combustion contributed less than 2 percent to\\nnational total NH 3 emissions throughout the 1990s.\\nHistorically, residential wood contributes the largest\\nquantity of fuel combustion CO and VOC emissions.\\nTherefore, despite a gradual increase in CO and VOC\\nemissions from electric utilities and industrial sources since\\n1940, the more substantial decline in emissions from\\nresidential wood consumption since 1985 accounts for the\\noverall decline from the fuel combustion category since 1985.\\nCO and VOC emissions from the fuel combustion category\\naccounted for 16 and 12 percent of total national CO and VOC\\nemissions in 1940 but only 6 and 5 percent in 1998.\\nIn 1900, emissions from all fuel combustion sources\\nrepresented 68 percent of total national VOC emissions, with\\nresidential wood combustion accounting for 90 percent of\\nthose emissions. From 1940 to 1970, residential wood\\nconsumption declined steadily as a result of the abundant\\nsupply, low relative prices, and convenience of fossil fuels\\nrelative to wood for home heating, cooking, and heating water.\\nThis decline halted in the early 1970s because disruptions in\\ncrude oil deliveries and related product markets caused prices\\nfor fossil fuel products to rise. These higher prices led to a\\nresurgence in the use of wood for home heating and thus to a\\ncorresponding increase in emissions from residential wood\\ncombustion. By 1980, though, prices of fossil fuel products\\nonce again began to decline. As a result, residential wood\\nconsumption once again declined, as did the corresponding\\nCO and VOC emissions.\\nWith regard to NO x electric utilities contribute the largest\\npercentage of NO x emissions from the stationary source fuel\\ncombustion categories. In 1900, electric utilities accounted for\\n4 percent of total national 1998 NO x emissions, but by 1998\\nthey accounted for 25 percent of total national NO x emissions.\\nCoal accounted for 88 percent of the electric utility NO x\\nemissions in 1998.\\nFuel combustion-industrial contributes approximately 12\\npercent of total national 1998 NO x emissions. While\\nemissions from this source have generally declined since 1970,\\nthey rose slightly from 1992 to 1996 (see Appendix Table A-\\n2). Meanwhile, NO x emissions from fuel combustion other\\ngenerally increased since 1940, although a small decline has\\noccurred since 1992. Fuel combustion-other contributed less\\nthan 5 percent of total national NO x emissions in 1998.\\nAs with NO x emissions, electric utilities contributed 4\\npercent of total national S0 2 emissions in 1900. These\\nemissions increased by a factor of 5 over the period 1900 to\\n1925, but the onset of the Great Depression put a halt to the\\ngrowth in these emissions during the 1930s. As the United\\nStates recovered from the Depression, emissions from electric\\nutilities once again rose. By 1940, SO, emissions levels\\napproximated pre-1930 levels. From 1940 to 1970, SO,\\nemissions from electric utilities doubled every decade as a\\nresult of increased coal consumption. By 1970, emissions\\nfrom coal combustion accounted for more than 90 percent of\\ntotal SO, emissions from electric utilities. With the help of\\nregulatory controls, SO, emissions from electric utilities using\\nall types of energy sources decreased approximately 38\\npercent from 1970 to 1996 (see Table A-4). Despite this\\ndecrease, electric utilities still accounted for 67 percent of the\\ntotal national SO, emissions in 1998.\\nIn 1940, PM 10 emissions from fuel combustion\\nrepresented approximately 31 percent of nonfugitive dust\\nPM 10 emissions. Electric utility PM 10 emissions derive\\nprimarily from the combustion of coal. Emissions from this\\nelectric utilities increased by approximately 85 percent\\nbetween 1940 and 1970, which corresponds to an increase in\\nelectric production using coal as an energy source during the\\nsame time period. Fuel combustion PM ^emissions have since\\ndeclined from 1970 levels. In terms of PM, 5 overall fuel\\ncombustion emissions remained fairly steady from 1990\\nthrough 1998. Fuel combustion sources contributed 9 percent\\nof total national 1998 PM 2 5 emissions\\nFuel combustion sources accounted for 5 percent of total\\nnational Pb emissions in 1970. Despite a 95 percent decline\\nsince 1970, fuel combustion sources still accounted for 13\\npercent of total national Pb emissions in 1998. Fuel\\ncombustion\u00e2\u0080\u0099s contribution to total NH, emissions remained\\nless than 2 percent throughout the 1990 to 1998 time frame.\\nThe overall decline in emissions from fuel combustion\\nsources since the 1970s can be attributed to various regulatory\\nactions. As mentioned previously, SO, emissions from\\nelectric utilities using all types of energy sources decreased\\napproximately 24 percent from 1970 to 1998. The SO,\\n3-4 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0062.jp2"}, "63": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nNAAQS, promulgated in 1971, served as a primary factor in\\nreducing S0 2 emissions. Another factor was EPA\u00e2\u0080\u0099s\\ndevelopment of a NSPS in 1971. This NSPS required that all\\nnew coal-fired power plants emit no more than 1.2 pounds of\\nSO, per each million British thermal units (Btus) of electricity\\nproduced. Most new plants chose to meet this NSPS by\\nshifting to lower-sulfur coals. An amendment to the CAA in\\n1977 effectively required any new coal-fired power plant not\\nonly to meet the original NSPS, but also to use some form of\\nscrubbing equipment, even when using low-sulfur coal.\\nBeginning in December 1976, a NSPS for new, modified, or\\nreconstructed fossil-fuel-fired steam generators became\\neffective, further promoting reductions in fuel combustion\\nemissions. To help reduce PM emissions, EPA promulgated\\na TSP NAAQS in 1971. In 1987, EPA revised the TSP\\nstandard to include only PM 10\\nAs a result of EPA\u00e2\u0080\u0099s regulations, SO, and PM 10 emissions\\nfrom coal-fired electric power facilities fell by 8 and 85\\npercent, respectively, between 1970 and 1993, despite the fact\\nthat consumption of coal to produce electricity increased 150\\npercent during that same period. 2\\nTitle IV (Acid Deposition Control) of the CAAA is an\\nimportant factor in the decline in SO, emissions from fuel\\ncombustion sources and has contributed to the general decline\\nof NO x emissions. Title IV specifies that annual SO,\\nemissions must decrease by 10 million tons from 1980\\nemissions levels and suggests, as a guideline, that annual NO x\\nemissions be reduced by 2 million tons from 1980 levels. Title\\nIV defines two stages by which SO, reductions must occur.\\nPhase I, which affects 263 mostly coal-fired units, began\\nJanuary 1, 1995. Phase II, which applies to the remaining\\naffected Title IV units, began January 1, 2000. To achieve\\nthese reductions in a cost effective manner, utilities may\\nchoose from among a variety of possibilities, including\\nparticipating in a market-based allowance trading system. 3\\nMany utilities switched to low sulfur coal and some\\ninstalled Hue gas desulfurization equipment (also known as\\nscrubbers) for their Phase I units, thereby achieving reductions\\nin S0 2 emissions greater than those required under Title IV.\\nThese changes enabled utilities to reduce SO, emissions from\\ntheir Phase I units from 7.4 million tons in 1994 to 4.5 million\\ntons in 1995, the first year of compliance.\\n3.4.2 How Have Emissions in the Industrial\\nProcess Categories Changed?\\nIndustrial processes include the following Tier 1\\ncategories: chemical and allied products; metals processing;\\npetroleum and related industries; other industrial processes;\\nsolvent utilization; storage and transport; and waste disposal\\nand recycling.\\nCO, NO x and VOC emissions from industrial processes\\npeaked in 1950, 1960, and 1980, respectively. Industrial\\nprocesses accounted for 12 percent of total national CO\\nemissions in 1940 and 13 percent in 1970, but only 5 percent\\nof total national CO emissions in 1998. With regard to NO x\\nemissions, industrial processes historically account for only a\\nsmall percentage of the national total. Industrial processes\\naccounted for an increasing share of national VOC emissions\\nbetween 1900 and 1970. Although VOC emissions from\\nindustrial process sources declined by 41 percent from 1970\\nto 1998, they still account for 47 percent of total national VOC\\nemissions. Emission control devices and process changes\\ncontributed to the decline in actual VOC emissions since\\n1970.\\nCO emissions from petroleum and related industries\\nincreased by a factor of 10 between 1940 and 1970 due to\\nincreases in refinery throughput and in demand for refined\\npetroleum products. Since 1970, CO emissions from the\\npetroleum refining industry have decreased by 83 percent due\\nto the installation of emission control devices such as fluid\\ncatalytic cracking units and the retirement of obsolete high\\npolluting processes such as the manufacture of carbon black\\nby channel process. By 1998, petroleum refining accounted\\nfor less than 1 percent of total national CO emissions.\\nAs mentioned previously, industrial processes account for\\nonly a small percentage of the national total NO x emissions.\\nWithin the industrial process category, though, waste disposal\\nand recycling contributed the highest percentage of NO x\\nemissions from 1940 to 1970. NO x emissions from the waste\\ndisposal and recycling category increased by 300 percent from\\n1940 to 1970, but then decreased by 78 percent from 1970 to\\n1998 to less than 1940 levels. After 1970, the other industrial\\nprocesses category surpassed waste disposal and recycling as\\nthe biggest contributor of industrial process NO x emissions.\\nThe 34 percent increase in NO x emissions from industrial\\nprocesses from 1980 to 1998 occurred partly because of a\\nchange in the methodology used to estimate emissions\\nbetween 1984 and 1985.\\nEmissions of VOCs from petroleum and related industries\\nand petroleum product storage and marketing operations\\nincreased during the mid-1970s as a result of increased\\ndemand for petroleum products, especially motor gasoline.\\nAfter 1980, the emissions from these sources decreased as the\\nresult of product reformulation and the implementation of\\npollutant control measures.\\nIndustrial process S0 2 emissions peaked in 1970, when\\nthey contributed approximately 23 percent of the total national\\nSO, emissions. From 1970 to 1998, emissions decreased by\\n79 percent, and by 1998 industrial processes only contributed\\n8 percent of the national total SO, emissions.\\nA major reason for the decline in industrial process SO,\\nemissions since 1970 comes from the decline in metals\\nprocessing emissions. Although SO, emissions from metals\\nprocessing increased by 44 percent over the period 1940 to\\n1970, they decreased by almost 91 percent from 1970 through\\n1998 due to the increased use of emission control devices. By\\n1998, metals processing accounted for approximately 2\\npercent of total national S0 2 emissions in 1998, down from 15\\npercent in 1970. In addition, S0 2 emissions from nonferrous\\n3.0 Summary of National Emissions Trends 3-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0063.jp2"}, "64": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nsmelters have fallen significantly. By-product recovery of\\nsulfuric acid at these smelters has increased since 1970,\\nresulting in the recovered sulfuric acid not being emitted as\\nS0 2\\nHistorically, copper processing contributed the largest\\npercentage of metals processing S0 2 emissions. To control\\ncopper processing S0 2 emissions, EPA issued a NSPS to\\nregulate SO, emissions from copper smelters built, modified,\\nor reconstructed after October 16, 1974. As a result, S0 2\\nemissions from copper production facilities declined almost 97\\npercent between 1970 and 1998, even though copper\\nproduction only declined by 15 percent during the time period\\n(1970 to 1993). 4\\nEmissions of SO, from chemical and allied\\nmanufacturing, petroleum and related industries, and other\\nindustrial processes accounted for 4 percent of total SO,\\nemissions in 1940 and 7 percent in 1970. Since 1970, S0 2\\nemissions from these sources have declined by 56 percent. The\\nNSPS issued for sulfuric acid manufacturing plants built,\\nmodified, or reconstructed after 1972 is one major factor\\ncontributing to this decline.\\nPM 10 emissions from industrial processes increased from\\n1940 to 1960, primarily as a result of increased industrial\\nproduction. From 1960 to 1970, industrial output continued\\nto grow, but PM 10 emissions began to decline due to the\\ninstallation of pollution control equipment mandated by state\\nand local air pollution control programs. This decline was\\nvery slight, though, because the rise in emissions due to\\nproduction increases more than offset the decline in emissions\\ncaused by the control devices.\\nIn 1970, industrial processes contributed 66 percent of\\ntotal national nonfugitive dust source PM 10 emissions. By\\n1998, this contribution had decreased to 26 percent, reflecting\\nthe significant progress achieved in reducing emissions from\\nindustrial processes.\\nPM 2 5 emissions from industrial processes have remained\\nfairly steady throughout the 1990s, although emissions from\\nall industrial process categories declined slightly between\\n1995 and 1998.\\nIn 1970, the industrial process group\u00e2\u0080\u0099s Pb emissions were\\n13 percent of almost 221 thousand tons, nationally. Seventy-\\neight percent of this national total came from the on-road\\nvehicles category which, by 1998 had been reduced to a mere\\n19 tons per year. Thus, while industrial process emissions of\\nPb have been reduced by 90 percent by 1998, they now\\nrepresent 74 percent of the more dramatically reduced national\\ntotal of less than 4 thousand tons per year.\\nSimilar to PM 25 emissions, emissions of NH 3 from\\nindustrial process remained fairly steady throughout the 1990s.\\nEmissions from all industrial process categories except other\\nindustrial processes declined slightly between 1995 and 1998.\\n3.4.3 How Have Emissions in the On-road\\nVehicle Categories Changed?\\nHistorically, on-road vehicles have contributed significant\\namounts to national CO, NO x VOC, PM (if only nonfugitive\\ndust emissions are considered), and Pb emissions levels but\\nonly small amounts to national SO, emission levels. The\\nincreasing popularity of motorized vehicles during the first\\nhalf of the 20 th century led to a corresponding increase in\\nemissions from these vehicles.\\nMotorized vehicles became so popular that by 1970, on\u00c2\u00ac\\nroad vehicles accounted for 35 percent of total NO x emissions,\\n68 percent of total CO emissions, 42 percent of total VOC\\nemissions, and 78 percent of total Pb emissions.\\nIn an effort to control rising emissions levels, in the early\\n1970s EPA developed CO, NO x and VOC emission limits for\\non-road vehicles. Table 3-9 lists the CO emission standards,\\nexpressed in grams per mile (gpm), for light-duty vehicles\\n(LDV) and light-duty trucks (LDT). Table 3-10 and Table\\n3-11 list the NO x and VOC emissions limits for LDVs and\\nLDTs, respectively. In addition to these limits, LDTs greater\\nthan 6,000 pounds and heavy-duty trucks must also meet NO x\\nemissions standards. The Federal CO standards through 1975\\napplied only to gasoline-powered LDTs, whereas federal\\nstandards for 1976 and later applied to both gasoline and\\ndiesel-powered LDTs. In addition, EPA requires that 1984\\nand later model years meet a CO standard of 0.50 percent at\\nidle (effective with the 1988 model year at higher altitudes).\\nSimilar to the NO x standards, other CO standards apply to\\nLDTs more than 6,000 lbs, heavy-duty engines and vehicles,\\nand non-road engines and vehicles.\\nWith regard to additional CO emissions controls, the\\nCAAA requires cars to meet a standard of 10 gpm at 20\\ndegrees Fahrenheit, starting with the 1996 model year. This\\nstandard helps ensure that vehicular emission control devices\\nwork efficiently at low temperatures.\\nIn general, the emission limits set by EPA resulted in\\nsignificant decreases since 1970 in CO and VOC emitted by\\non-road vehicles. Since 1970, CO and VOC emissions from\\non-road vehicles have declined by almost 43 and 59 percent,\\nrespectively. NO x emissions from on-road vehicles peaked in\\nthe late 1970s but have declined slightly since then. Although\\nNO x emissions levels from on-road vehicles are slightly higher\\nthan in 1970, VMT has more than doubled since 1970. The\\nfederal NO x emissions standards have succeeded in keeping\\nemissions growth in check.\\nTo achieve more significant NO x emissions reductions,\\nEPA issued new federal tailpipe emissions standards in\\nDecember 1999 for passenger cars, light trucks, and larger\\npassenger vehicles. These standards, known as Tier II\\nstandards, should help reduce air pollution. These standards\\nwill take effect beginning in 2004 and will apply to both cars\\nand light-duty trucks, including sport utility vehicles (SUVs).\\nUnder the Tier II standards, affected vehicles must meet\\na 0.07 gpm standard for NO x which is a 77 percent reduction\\n3-6 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0064.jp2"}, "65": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nfor cars and up to a 95 percent reduction for LDTs and SUVs.\\nVehicles weighing less than 6000 pounds will be phased-in to\\nthe new standard between 2004 and 2007. The heaviest LDTs\\nwill adopt a three-step approach, spanning from 2004 to 2009.\\nWhen it issued the Tier II standards, EPA also set new\\nstandards for sulfur levels in gasoline. Gasoline suppliers\\nmust meet an average sulfur level of 30 ppm by 2005, down\\nfrom the current average of 300 ppm. The new sulfur levels\\nwill ensure the effectiveness of low emission-control\\ntechnologies in vehicles. Auto makers and refiners will be\\nallowed to meet these standards by averaging across the entire\\nvehicle fleet and gasoline pool.\\nPb emissions from on-road vehicles, which peaked in the\\nearly 1970s, have steadily decreased as the result of a series of\\nregulatory actions that progressively reduced the Pb content of\\nall gasoline. EPA mandates reduced the Pb content of\\ngasoline dramatically, from an average of 1.0 gram per gallon\\n(gpg) to 0.5 gpgon July 1, 1985, and still further to 0.1 gpgon\\nJanuary 1, 1986. In addition, as part of EPA s overall\\nautomotive emission control program, unleaded gasoline was\\nintroduced in 1975 for use in automobiles equipped with\\ncatalytic control devices, which help reduce CO, VOC, and\\nNO x emissions. In 1975, unleaded gasoline\u00e2\u0080\u0099s share of the total\\ngasoline market totaled 13 percent. By 1982 this share had\\nclimbed to approximately 50 percent, and by 1996 (due to the\\nCAAA prohibition on the use of leaded gasoline in highway\\nvehicles after December 31, 1995) unleaded gasoline\\naccounted for 100 percent of the total gasoline market.\\nTable A-6 (see Appendix A) shows that Pb emissions\\ndecreased dramatically between 1990 and 1991. This decrease\\nis the result of large changes in the values for Pb in gasoline.\\nSince the prohibition on Pb in gasoline did not officially begin\\nuntil January 1, 1996, the reductions calculated for 1991 and\\nlater are primarily the result of limited data on trace Pb levels\\nin gasoline for these years. Therefore, the full reduction that\\nbegins in 1991 may actually occur several years later.\\nPb emissions from on-road vehicles have fallen\\nsignificantly since the introduction of these regulations, and Pb\\nemissions from on-road vehicles now account for less than 1\\npercent of national Pb emissions, down substantially from\\nalmost 82 percent of national emissions in 1980.\\nIn an effort to reduce SO, and PM (as sulfate particles)\\nemissions from on-road vehicles, EPA published a regulation\\non August 21, 1990, that governs desulfurization of diesel\\nmotor fuel. This regulation states that as of October 1, 1993,\\nall diesel fuel that contains a concentration of sulfur in excess\\nof 0.05 percent by weight or that fails to meet a minimum\\ncetane index of 40 cannot be used in motor vehicles. 5 Since\\nimplementation of these desulfurization regulations, EPA has\\nfound that SO, emissions from diesel motor vehicles are\\nreduced by approximately 75 percent.\\nIn 1940, on-road vehicles accounted for just over 1\\npercent of nonfugitive dust PM 10 emissions. Although the\\n1998 emissions from on-road vehicles represent 9 percent of\\nthe total national PM 10 emissions from nonfugitive dust\\nsources, PM 10 emissions from on-road vehicles ini998 are\\napproximately the same as those in 1940.\\nAbsent regulation, it is reasonable to assume that a\\ndecrease in the price of gasoline will result in greater VMT,\\nincreased fuel use, and greater emissions, all other factors\\nremaining unchanged. However, overall on-road vehicle\\nemissions actually declined from 1970 to 1998, despite the\\nfact that fuel use increased approximately 50 percent, VMT\\nincreased over 100 percent, and real gasoline prices decreased\\n17 percent during this same time period. 1 These trends\\nindicate the success of regulations in reducing emissions from\\non-road vehicles.\\n3.4.4 How Have Emissions in the Non-road\\nEngines and Vehicle Categories\\nChanged?\\nUnlike emissions trends for on-road vehicles, emissions\\nof CO, NO x and VOC from non-road engines and vehicles\\nincreased steadily from 1940 to 1996, with slight reductions in\\nCO and VOC emissions over the past 2 years. SO, emissions\\ndeclined by 97 percent from 1940 to 1970, but have since risen\\nagain, to about one third of 1940 levels. PM 10 emissions\\ndeclined significantly from 1940 to 1960, rose slightly in the\\nperiod from 1960 to 1990, and have declined slightly since\\n1990. PM, 5 emissions have remained relatively level for the\\npast 8 years. Pb emissions declined approximately 91 percent\\nbetween 1970 and 1985, and they have continued to decline\\nslightly since 1985. NH 3 emissions from non-road engines\\nand vehicle over the past 9 years are quite negligible.\\nNon-road engines and vehicles contributed 9 percent of\\ntotal national CO emissions in 1940, with emissions from\\nrailroad locomotives accounting for approximately 51 percent\\nof this amount. CO emissions from non-road vehicles and\\nengines have increased 90 percent from 1940 levels and now\\naccount for 22 percent of the national total, but now non-road\\ngasoline equipment engines are the predominant sources of\\nnon-road CO emissions.\\nIn 1900, non-road engines and vehicles accounted for 4\\npercent of total national VOC emissions, of which railroad\\nemissions contributed 99 percent. Railroad VOC emissions\\npeaked in 1920 at 20 percent of the national total and have\\ndecreased since then to less than 1 percent currently.\\nAlthough railroad emissions decreased, emissions from non\u00c2\u00ac\\nroad engines and vehicles increased 216 percent during the\\n1940 to 1998 period. As a result, emissions from non-road\\nengines and vehicles as a percentage of the national total\\nclimbed from approximately 5 percent in 1940 to\\napproximately 14 percent in 1998.\\nSimilarly to on-road vehicle NO x emissions trends,\\nemissions from non-road engines and vehicles increased over\\nthe period from 1940 to 1998. To help slow this growth in\\nemissions, EPA established emission control measures (Tier\\nI standards) for new non-road diesel engines in certain\\nhorsepower categories. These standards began to take effect\\n3.0 Summary of National Emissions Trends 3-7", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0065.jp2"}, "66": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nin 1996, with full phase-in for all horsepower categories\\nscheduled for 2000. These controls should help reduce the\\namount of NO x emissions emitted by these sources.\\nIn 1940, S0 2 and PM 10 emissions from non-road vehicles\\nand engines both accounted for approximately 16 percent,\\nrespectively, of total national emissions for these two\\npollutants. Railroads contributed significantly to total 1940\\nSO, and PM 10 emissions. From 1940 to 1970, S0 2 and PM 10\\nemissions from railroads decreased by 99 percent as a result of\\nthe obsolescence of coal-fired locomotives. By 1998, non\u00c2\u00ac\\nroad engines and vehicles represented only 1 percent of the\\ntotal 1998 national PM 10 emissions (16 percent of nonfugitive\\ndust sources). While PM 10 emissions from non-road engines\\nand vehicles declined, so did PM 10 emissions from most other\\nnonfugitive dust sources.\\n3.4.5 How Have Emissions in the\\nMiscellaneous Categories Changed?\\nIn 1940, CO emissions from \u00e2\u0080\u009cmiscellaneous other\\ncombustion forest wildfires\u00e2\u0080\u009d accounted for 27 percent of\\ntotal national CO emissions. Although relatively erratic from\\nyear to year due to the uncontrolled nature of wildfires,\\nwildfire CO emissions declined from 1940 levels to only 3\\npercent of total national CO emissions in 1998. Similarly,\\nannual PM 10 emissions from wildfires vary depending upon\\nthe incidence of wildfires and upon weather conditions in\\nforested areas.\\nMiscellaneous source emissions accounted for 13 percent\\nof the total 1940 NO x emissions. In 1998, the total emissions\\nfor the miscellaneous sources accounted for slightly more than\\n1 percent of national NO x emissions.\\nIn 1900, emissions from the miscellaneous sources\\ncategory represented 24 percent of total VOC emissions. By\\n1998 they accounted for only 4 percent of national VOC\\nemissions. With regard to S0 2 emissions, miscellaneous\\nsources accounted for less than 3 percent of total national SO,\\nemissions in 1940. By 1998, they contributed less than 0.1\\npercent of national S0 2 emissions. Pb emissions from other/\\nmiscellaneous sources account for a negligible amount ot\\nnational Pb emissions. Meanwhile, miscellaneous emissions\\naccount for a substantial percentage of NH 3 emissions. From\\n1990 to 1998, emissions from miscellaneous sources rose 13\\npercent, and they accounted for 86 percent of total national\\nNH 3 emissions in both 1990 and 1998.\\n3.5 HOW HAVE EMISSIONS IN THE\\nFUGITIVE DUST CATEGORIES\\nCHANGED?\\nFugitive dust source emission estimates were first\\npresented in the 1991 Trends report. At that time, EPA based\\nits emission estimates upon old emission factors and limited\\ndata. The methods EPA used to produce the estimates relied\\non State-level default data for most source categories. In the\\n1997 Trends report, EPA revised the methods used to produce\\npost-1989 estimates in order to reflect improved emission\\nfactors, improved activity data, or both.\\nFor several source categories, the methodology for\\nestimating fugitive dust emissions utilizes meteorological data\\nsuch as the number of days with greater than 0.01 inches of\\nprecipitation and average monthly wind speed. These data can\\nvary significantly from year-to-year, resulting in highly\\nvariable emissions.\\nPM I0 and PM, 5 fugitive dust emissions can be determined\\nfrom Tables 3-5 and 3-6 respectively. The categories that\\ncomprise the fugitive dust emission categories are identified\\nin Chapter 1, section 1.4. As previously noted, estimates of\\nPM 10 fugitive dust prior to 1989 were based on crude\\nmethodologies and should be strongly discounted. PM 10\\nemissions from fugitive dust sources decreased by 24 percent\\nfrom 1985 to 1998 due primarily to the changes in emission\\nmethodologies for several of the fugitive dust sources, but also\\ndue to holding wind erosion constant from 1996 forward.\\nFor 1998, EPA estimates total national fugitive dust PM, 0\\nand PM, 5 emissions to be approximately 8 and 2 times higher,\\nrespectively, than total national nonfugitive PM 10 and PM 25\\nemissions.\\n3.6 REFERENCES\\n1. \u00e2\u0080\u009cEnergy Statistics Sourcebook,\u00e2\u0080\u009d Ninth Edition, Pennwell Publishing. August 1994.\\n2. \u00e2\u0080\u009cElectric Power Monthly,\u00e2\u0080\u009d Energy Information Administration, U.S. Department of Energy, Washington, DC, various\\neditions.\\n3. \u00e2\u0080\u009c1995 Compliance Results,\u00e2\u0080\u009d Acid Rain Program, EPA-430/R-96-012, Office of Air and Radiation, U.S. Environmental\\nProtection Agency, Washington, DC. July 1996.\\n4. \u00e2\u0080\u009cCement,\u00e2\u0080\u009d Minerals Yearbook, U.S. Department of Interior, Bureau of Mines, Washington, DC, various years.\\n5. \u00e2\u0080\u009cDevelopment of an Industrial SO, Emissions Inventory Baseline and 1995 Report to Congress,\u00e2\u0080\u009d U.S. Environmental\\nProtection Agency, Research Triangle Park, NC. December 1994.\\n3-8 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0066.jp2"}, "67": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-1. Total National Emissions of Carbon Monoxide, 1940 through 1998\\n(thousand short tons)\\nSource Category\\n1940\\n1950\\n1960\\n1970\\n1980\\n1990\\n1996\\n1998\\nFUEL COMB. ELEC. UTIL.\\n4\\n110\\n110\\n237\\n322\\n363\\n391\\n417\\nFUEL COMB. INDUSTRIAL\\n435\\n549\\n661\\n770\\n750\\n879\\n1,155\\n1,115\\nFUEL COMB. OTHER\\n14,890\\n10,656\\n6,250\\n3,625\\n6,230\\n4,269\\n4,603\\n3,843\\nResidential Wood\\n11,279\\n7,716\\n4,743\\n2,932\\n5,992\\n3,781\\n4,200\\n3,452\\nCHEMICAL ALLIED PRODUCT MFG\\n4,190\\n5,844\\n3,982\\n3,397\\n2,151\\n1,183\\n1,100\\n1,129\\nOther Chemical Mfg\\n4,139\\n5,760\\n3,775\\n2,866\\n1,417\\n854\\n870\\n893\\ncarbon black mfg\\n4,139\\n5,760\\n3,775\\n2,866\\n1,417\\n798\\n841\\n863\\nMETALS PROCESSING\\n2,750\\n2,910\\n2,866\\n3,644\\n2,246\\n2,640\\n1,429\\n1,495\\nNonferrous Metals Processing\\n36\\n118\\n326\\n652\\n842\\n436\\n442\\n446\\nFerrous Metals Processing\\n2,714\\n2,792\\n2,540\\n2,991\\n1,404\\n2,163\\n944\\n1,006\\nbasic oxygen furnace\\nNA\\nNA\\n23\\n440\\n80\\n594\\n117\\n126\\nPETROLEUM RELATED INDUSTRIES\\n221\\n2,651\\n3,086\\n2,179\\n1,723\\n333\\n356\\n368\\nOil Gas Production\\nNA\\nNA\\nNA\\nNA\\nNA\\n38\\n26\\n27\\nPetroleum Refineries Related Industries\\n221\\n2,651\\n3,086\\n2,168\\n1,723\\n291\\n322\\n334\\nfee units\\n210\\n2,528\\n2,810\\n1,820\\n1,680\\n284\\n311\\n322\\nOTHER INDUSTRIAL PROCESSES\\n114\\n231\\n342\\n620\\n830\\n537\\n600\\n632\\nWood, Pulp Paper, Publishing Products\\n110\\n220\\n331\\n610\\n798\\n473\\n391\\n416\\nsulfate pulping: rec. furnace/evaporator\\nNA\\nNA\\nNA\\nNA\\nNA\\n370\\n305\\n325\\nSOLVENT UTILIZATION\\nNA\\nNA\\nNA\\nNA\\nNA\\n5\\n2\\n2\\nSTORAGE TRANSPORT\\nNA\\nNA\\nNA\\nNA\\nNA\\n76\\n78\\n80\\nWASTE DISPOSAL RECYCLING\\n3,630\\n4,717\\n5,597\\n7,059\\n2,300\\n1,079\\n1,127\\n1,154\\nIncineration\\n2,202\\n2,711\\n2,703\\n2,979\\n1,246\\n372\\n404\\n413\\nresidential\\n716\\n824\\n972\\n1,107\\n945\\n294\\n330\\n336\\nOpen Burning\\n1,428\\n2,006\\n2,894\\n4,080\\n1,054\\n706\\n111\\n735\\nresidential\\nNA\\nNA\\nNA\\nNA\\nNA\\n509\\n515\\n524\\nON-ROAD VEHICLES\\n30,121\\n45,196\\n64,266\\n88,034\\n78,049\\n57,848\\n53,262\\n50,386\\nLight-Duty Gas Vehicles Motorcycles\\n22,237\\n31,493\\n47,679\\n64,031\\n53,561\\n37,407\\n28,732\\n27,039\\nlight-duty gas vehicles\\n22,232\\n31,472\\n47,655\\n63,846\\n53,342\\n37,198\\n28,543\\n26,848\\nLight-Duty Gas Trucks\\n3,752\\n6,110\\n7,791\\n16,570\\n16,137\\n13,816\\n19,271\\n18,726\\nlight-duty gas trucks 1\\n2,694\\n4,396\\n5,591\\n10,102\\n10,395\\n8,415\\n11,060\\n10,826\\nlight-duty gas trucks 2\\n1,058\\n1,714\\n2,200\\n6,468\\n5,742\\n5,402\\n8,211\\n7,900\\nHeavy-Duty Gas Vehicles\\n4,132\\n7,537\\n8,557\\n6,712\\n7,189\\n5,360\\n3,766\\n3,067\\nDiesels\\nNA\\n54\\n239\\n721\\n1,161\\n1,265\\n1,493\\n1,554\\nheavy-duty diesel vehicles\\nNA\\n54\\n239\\n721\\n1,139\\n1,229\\n1,453\\n1,514\\nNON-ROAD ENGINES AND VEHICLES\\n8,051\\n11,610\\n11,575\\n11,970\\n14,489\\n18,191\\n20,232\\n19,914\\nNon-Road Gasoline\\n3,777\\n7,331\\n8,753\\n10,946\\n12,760\\n15,394\\n17,074\\n16,812\\nindustrial\\n780\\n1,558\\n1,379\\n535\\n709\\n723\\n592\\n563\\nlawn garden\\nNA\\nNA\\nNA\\n5,899\\n6,764\\n8,237\\n9,305\\n9,024\\nlight commercial\\nNA\\nNA\\nNA\\n1,905\\n2,095\\n2,877\\n3,514\\n3,566\\nrecreational marine vessels\\n60\\n120\\n518\\n1,763\\n1,990\\n2,117\\n2,142\\n2,156\\nNon-Road Diesel\\n32\\n53\\n65\\n430\\n829\\n1,098\\n1,282\\n1,180\\nconstruction\\n20\\n43\\n40\\n254\\n479\\n662\\n794\\n728\\nfarm\\n12\\n10\\n17\\n16\\n174\\n166\\n176\\n163\\nAircraft\\n4\\n934\\n1,764\\n506\\n743\\n904\\n949\\n955\\nRailroads\\n4,083\\n3,076\\n332\\n65\\n96\\n121\\n112\\n115\\nMISCELLANEOUS\\n29,210\\n18,135\\n11,010\\n7,909\\n8,344\\n11,122\\n11,144\\n8,920\\nOther Combustion\\n29,210\\n18,135\\n11,010\\n7,909\\n8,344\\n11,122\\n11,144\\n8,919\\nTOTAL ALL SOURCES\\n93,616\\n102,609\\n109,745\\n129,444\\n117,434\\n98,523\\n95,480\\n89,455\\nNote(s): NA not available. For several source categories, emissions either prior to or beginning with 1985 are not available at the more\\ndetailed level but are contained in the more aggregate estimate.\\n\u00e2\u0080\u009cOther\u00e2\u0080\u009d categories may contain emissions that could not be accurately allocated to specific source categories.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\n3.0 Summary of National Emissions Trends 3-9", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0067.jp2"}, "68": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-2. Total National Emissions of Nitrogen Oxides, 1940 through 1998\\n(thousand short tons)\\nSource Category\\n1940\\n1950\\n1960\\n1970\\n1980\\n1990\\n1996\\n1998\\nFUEL COMB. ELEC. UTIL.\\n660\\n1,316\\n2,536\\n4,900\\n7,024\\n6,663\\n6,057\\n6,103\\nCoal\\n467\\n1,118\\n2,038\\n3,888\\n6,123\\n5,642\\n5,542\\n5,395\\nbituminous\\n255\\n584\\n1,154\\n2,112\\n3,439\\n4,532\\n3,748\\n3,622\\nOil\\n193\\n198\\n498\\n1,012\\n901\\n221\\n103\\n208\\nresidual\\n6\\n23\\n8\\n40\\n39\\n207\\n101\\n206\\ndistillate\\n187\\n175\\n490\\n972\\n862\\n14\\n2\\n2\\nGas\\nNA\\nNA\\nNA\\nNA\\nNA\\n565\\n265\\n344\\nnatural\\nNA\\nNA\\nNA\\nNA\\nNA\\n565\\n264\\n342\\nFUEL COMB. INDUSTRIAL\\n2,543\\n3,192\\n4,075\\n4,325\\n3,555\\n3,035\\n3,072\\n2,969\\nCoal\\n2,012\\n1,076\\n782\\n771\\n444\\n585\\n567\\n548\\nOil\\n122\\n237\\n239\\n332\\n286\\n265\\n231\\n216\\nGas\\n365\\n1,756\\n2,954\\n3,060\\n2,619\\n1,182\\n1,184\\n1,154\\nnatural\\n337\\n1,692\\n2,846\\n3,053\\n2,469\\n967\\n978\\n943\\nInternal Combustion\\nNA\\nNA\\nNA\\nNA\\nNA\\n874\\n967\\n932\\nFUEL COMB. OTHER\\n529\\n647\\n760\\n836\\n741\\n1,196\\n1,224\\n1,117\\nCommercial/lnstitutional Gas\\n7\\n18\\n55\\n120\\n131\\n200\\n238\\n234\\nResidential Other\\n177\\n227\\n362\\n439\\n356\\n780\\n783\\n700\\nnatural gas\\n20\\n50\\n148\\n242\\n238\\n449\\n481\\n410\\nCHEMICAL ALLIED PRODUCT MFG\\n6\\n63\\n110\\n271\\n213\\n168\\n146\\n152\\nMETALS PROCESSING\\n4\\n110\\n110\\n77\\n65\\n97\\n83\\n88\\nPETROLEUM RELATED INDUSTRIES\\n105\\n110\\n220\\n240\\n72\\n153\\n134\\n138\\nOTHER INDUSTRIAL PROCESSES\\n107\\n93\\n131\\n187\\n205\\n378\\n386\\n408\\nMineral Products\\n105\\n89\\n123\\n169\\n181\\n270\\n286\\n303\\ncement mfg\\n32\\n55\\n78\\n97\\n98\\n151\\n172\\n182\\nSOLVENT UTILIZATION\\nNA\\nNA\\nNA\\nNA\\nNA\\n1\\n2\\n2\\nSTORAGE TRANSPORT\\nNA\\nNA\\nNA\\nNA\\nNA\\n3\\n7\\n7\\nWASTE DISPOSAL RECYCLING\\n110\\n215\\n331\\n440\\n111\\n91\\n95\\n97\\nON-ROAD VEHICLES\\n1,330\\n2,143\\n3,982\\n7,390\\n8,621\\n7,089\\n7,848\\n7,765\\nLight-Duty Gas Vehicles Motorcycles\\n970\\n1,415\\n2,607\\n4,158\\n4,421\\n3,220\\n2,979\\n2,849\\nlight-duty gas vehicles\\n970\\n1,415\\n2,606\\n4,156\\n4,416\\n3,208\\n2,967\\n2,837\\nLight-Duty Gas Trucks\\n204\\n339\\n525\\n1,278\\n1,408\\n1,256\\n1,950\\n1,917\\nlight-duty gas trucks 1\\n132\\n219\\n339\\n725\\n864\\n784\\n1,156\\n1,132\\nlight-duty gas trucks 2\\n73\\n120\\n186\\n553\\n544\\n472\\n794\\n785\\nHeavy-Duty Gas Vehicles\\n155\\n296\\n363\\n278\\n300\\n326\\n329\\n323\\nDiesels\\nNA\\n93\\n487\\n1,676\\n2,493\\n2,287\\n2,591\\n2,676\\nheavy-duty diesel vehicles\\nNA\\n93\\n487\\n1,676\\n2,463\\n2,240\\n2,544\\n2,630\\nNON-ROAD ENGINES AND VEHICLES\\n991\\n1,538\\n1,443\\n1,931\\n3,529\\n4,804\\n5,167\\n5,280\\nNon-Road Gasoline\\n122\\n249\\n312\\n85\\n101\\n120\\n132\\n159\\nNon-Road Diesel\\n103\\n187\\n247\\n1,109\\n2,125\\n2,513\\n2,786\\n2,809\\nconstruction\\n70\\n158\\n157\\n436\\n843\\n1,102\\n1,218\\n1,230\\nfarm\\n33\\n29\\n50\\n350\\n926\\n898\\n1,001\\n999\\nAircraft\\nNA\\n2\\n4\\n72\\n106\\n158\\n167\\n168\\nMarine Vessels\\n109\\n108\\n108\\n171\\n467\\n943\\n985\\n1,008\\nRailroads\\n657\\n992\\n772\\n495\\n731\\n929\\n922\\n947\\nMISCELLANEOUS\\n990\\n665\\n441\\n330\\n248\\n369\\n452\\n328\\nTOTAL ALL SOURCES\\n7,374\\n10,093\\n14,140\\n20,928\\n24,384\\n24,049\\n24,676\\n24,454\\nNote(s): N A not available. For several source categories, emissions either prior to or beginning with 1985 are not available at the more detailed\\nlevel but are contained in the more aggregate estimate.\\n\u00e2\u0080\u009cOther categories may contain emissions that could not be accurately allocated to specific source categories.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\n3-10 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0068.jp2"}, "69": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-3. Total National Emissions of Volatile Organic Compounds,\\n1940 through 1998 (thousand short tons)\\nSource Category\\n1940\\n1950\\n1960\\n1970\\n1980\\n1990\\n1996\\n1998\\nFUEL COMB. ELEC. UTIL.\\n2\\n9\\n9\\n30\\n45\\n47\\n49\\n54\\nFUEL COMB. INDUSTRIAL\\n108\\n98\\n106\\n150\\n157\\n182\\n166\\n161\\nFUEL COMB. OTHER\\n1,867\\n1,336\\n768\\n541\\n848\\n776\\n821\\n678\\nResidential Wood\\n1,410\\n970\\n563\\n460\\n809\\n718\\n759\\n620\\nCHEMICAL ALLIED PRODUCT MFG\\n884\\n1,324\\n991\\n1,341\\n1,595\\n634\\n388\\n396\\nMETALS PROCESSING\\n325\\n442\\n342\\n394\\n273\\n122\\n72\\n75\\nPETROLEUM RELATED INDUSTRIES\\n571\\n548\\n1,034\\n1,194\\n1,440\\n612\\n488\\n496\\nOTHER INDUSTRIAL PROCESSES\\n130\\n184\\n202\\n270\\n237\\n401\\n428\\n450\\nSOLVENT UTILIZATION\\n1,971\\n3,679\\n4,403\\n7,174\\n6,584\\n5,750\\n5,506\\n5,278\\nDegreasing\\n168\\n592\\n438\\n707\\n513\\n744\\n606\\n457\\nGraphic Arts\\n114\\n310\\n199\\n319\\n373\\n274\\n296\\n311\\nDry Cleaning\\n42\\n153\\n126\\n263\\n320\\n215\\n157\\n169\\npetroleum solvent\\nNA\\nNA\\nNA\\nNA\\nNA\\n104\\n92\\n99\\nSurface Coating\\n1,058\\n2,187\\n2,128\\n3,570\\n3,685\\n2,523\\n2,389\\n2,224\\nindustrial adhesives\\n14\\n41\\n29\\n52\\n55\\n390\\n356\\n160\\narchitectural\\n284\\nNA\\n412\\n442\\n477\\n495\\n484\\n491\\nNonindustrial\\n490\\nNA\\n\u00e2\u0080\u00a21,189\\n1,674\\n1,002\\n1,900\\n1,957\\n2,012\\ncutback asphalt\\n328\\nNA\\n789\\n1,045\\n323\\n199\\n135\\n144\\npesticide application\\n73\\nNA\\n193\\n241\\n241\\n258\\n386\\n405\\nadhesives\\nNA\\nNA\\nNA\\nNA\\nNA\\n361\\n307\\n313\\nconsumer solvents\\nNA\\nNA\\nNA\\nNA\\nNA\\n1,083\\n1,081\\n1,099\\nSTORAGE TRANSPORT\\n639\\n1,218\\n1,762\\n1,954\\n1,975\\n1,495\\n1,286\\n1,324\\nBulk Terminals Plants\\n185\\n361\\n528\\n599\\n517\\n359\\n211\\n217\\narea source: gasoline\\n158\\n307\\n449\\n509\\n440\\n282\\n163\\n167\\nPetroleum Petroleum Product Storage\\n148\\n218\\n304\\n300\\n306\\n157\\n172\\n178\\nPetroleum Petroleum Product Transport\\n57\\n100\\n115\\n92\\n61\\n151\\n118\\n122\\nService Stations: Stage 1\\n117\\n251\\n365\\n416\\n461\\n300\\n312\\n320\\nService Stations: Stage II\\n130\\n283\\n437\\n521\\n583\\n433\\n397\\n409\\nWASTE DISPOSAL RECYCLING\\n990\\n1,104\\n1,546\\n1,984\\n758\\n986\\n423\\n433\\nON-ROAD VEHICLES\\n4,817\\n7,251\\n10,506\\n12,972\\n8,979\\n6,313\\n5,490\\n5,325\\nLight-Duty Gas Vehicles Motorcycles\\n3,647\\n5,220\\n8,058\\n9,193\\n5,907\\n3,947\\n2,875\\n2,832\\nlight-duty gas vehicles\\n3,646\\n5,214\\n8,050\\n9,133\\n5,843\\n3,885\\n2,839\\n2,793\\nLight-Duty Gas Trucks\\n672\\n1,101\\n1,433\\n2,770\\n2,059\\n1,622\\n2,060\\n2,015\\nHeavy-Duty Gas Vehicles\\n498\\n908\\n926\\n743\\n611\\n432\\n293\\n257\\nDiesels\\nNA\\n22\\n89\\n266\\n402\\n312\\n263\\n222\\nNON-ROAD ENGINES AND VEHICLES\\n778\\n1,213\\n1,215\\n1,878\\n2,312\\n2,545\\n2,664\\n2,461\\nNon-Road Gasoline\\n208\\n423\\n526\\n1,564\\n1,787\\n1,889\\n1,982\\n1,794\\nlawn garden\\nNA\\nNA\\nNA\\n511\\n583\\n700\\n771\\n638\\nrecreational marine vessels\\n16\\n32\\n124\\n736\\n830\\n784\\n777\\n780\\nNon-Road Diesel\\n12\\n20\\n23\\n187\\n327\\n390\\n422\\n405\\nconstruction\\n6\\n15\\n13\\n94\\n135\\n181\\n206\\n199\\nfarm\\n6\\n5\\n8\\n39\\n138\\n126\\n120\\n111\\nAircraft\\n3\\n110\\n220\\n97\\n146\\n180\\n177\\n177\\nNATURAL SOURCES\\nNA\\nNA\\nNA\\nNA\\nNA\\n14\\n14\\n14\\nMISCELLANEOUS\\n4,079\\n2,530\\n1,573\\n1,101\\n1,134\\n1,059\\n940\\n772\\nOther Combustion\\n4,079\\n2,530\\n1,573\\n1,101\\n1,134\\n1,049\\n891\\n721\\nTOTAL ALL SOURCES\\n17,161\\n20,936\\n24,459\\n30,982\\n26,336\\n20,936\\n18,736\\n17,917\\nNote(s): NA not available. For several source categories, emissions either prior to or beginning with 1985 are not available at the more detailed\\nlevel but are contained in the more aggregate estimate.\\n\u00e2\u0080\u009cOther\u00e2\u0080\u009d categories may contain emissions that could not be accurately allocated to specific source categories.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\n3.0 Summary of National Emissions Trends 3-11", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0069.jp2"}, "70": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-4. Total National Emissions of Sulfur Dioxide, 1940 through 1998\\n(thousand short tons)\\nSource Category\\n1940\\n1950\\n1960\\n1970\\n1980\\n1990\\n1996\\n1998\\nFUEL COMB. ELEC. UTIL.\\n2,427\\n4,515\\n9,263\\n17,398\\n17,469\\n15,909\\n12,631\\n13,217\\nCoal\\n2,276\\n4,056\\n8,883\\n15,799\\n16,073\\n15,220\\n12,137\\n12,426\\nbituminous\\n1,359\\n2,427\\n5,367\\n9,574\\nNA\\n13,371\\n8,931\\n9,368\\nsubbituminous\\n668\\n1,196\\n2,642\\n4,716\\nNA\\n1,415\\n2,630\\n2,440\\nanthracite lignite\\n249\\n433\\n873\\n1,509\\nNA\\n434\\n576\\n618\\nOil\\n151\\n459\\n380\\n1,598\\n1,395\\n639\\n436\\n730\\nresidual\\n146\\n453\\n375\\n1,578\\nNA\\n629\\n430\\n726\\nFUEL COMB. INDUSTRIAL\\n6,060\\n5,725\\n3,864\\n4,568\\n2,951\\n3,550\\n3,022\\n2,895\\nCoal\\n5,188\\n4,423\\n2,703\\n3,129\\n1,527\\n1,914\\n1,465\\n1,415\\nbituminous\\n3,473\\n2,945\\n1,858\\n2,171\\n1,058\\n1,050\\n1,031\\n1,000\\nOil\\n554\\n972\\n922\\n1,229\\n1,065\\n927\\n844\\n773\\nresidual\\n397\\n721\\n663\\n956\\n851\\n687\\n637\\n568\\ndistillate\\n9\\n49\\n42\\n98\\n85\\n198\\n187\\n184\\nGas\\n145\\n180\\n189\\n140\\n299\\n543\\n556\\n558\\nFUEL COMB. OTHER\\n3,642\\n3,964\\n2,319\\n1,490\\n971\\n831\\n667\\n609\\nCommercial/Institutional Coal\\n695\\n1,212\\n154\\n109\\n110\\n212\\n177\\n194\\nCommercial/lnstitutional Oil\\n407\\n658\\n905\\n883\\n637\\n425\\n338\\n275\\nResidential Other\\n2,517\\n2,079\\n1,250\\n492\\n211\\n175\\n131\\n121\\nbituminous/subbituminous coal\\n2,267\\n1,758\\n868\\n260\\n43\\n30\\n17\\n18\\nCHEMICAL ALLIED PRODUCT MFG\\n215\\n427\\n447\\n591\\n280\\n297\\n291\\n299\\nInorganic Chemical Mfg\\n215\\n427\\n447\\n591\\n271\\n214\\n204\\n210\\nsulfur compounds\\n215\\n427\\n447\\n591\\n271\\n211\\n202\\n208\\nMETALS PROCESSING\\n3,309\\n3,747\\n3,986\\n4,775\\n1,842\\n726\\n429\\n444\\nNonferrous Metals Processing\\n2,760\\n3,092\\n3,322\\n4,060\\n1,279\\n517\\n283\\n288\\ncopper\\n2,292\\n2,369\\n2,772\\n3,507\\n1,080\\n323\\n114\\n119\\nlead\\n80\\n95\\n57\\n77\\n34\\n129\\n111\\n110\\nFerrous Metals Processing\\n550\\n655\\n664\\n715\\n562\\n186\\n128\\n139\\nPETROLEUM RELATED INDUSTRIES\\n224\\n340\\n676\\n881\\n734\\n430\\n337\\n345\\nOil Gas Production\\nNA\\n14\\n114\\n111\\n157\\n122\\n95\\n96\\nnatural gas\\nNA\\n14\\n114\\n111\\n157\\n120\\n95\\n95\\nPetroleum Refineries Related Industries\\n224\\n326\\n562\\n770\\n577\\n304\\n234\\n241\\nfluid catalytic cracking units\\n220\\n242\\n383\\n480\\n330\\n183\\n153\\n158\\nOTHER INDUSTRIAL PROCESSES\\n334\\n596\\n671\\n846\\n918\\n399\\n350\\n370\\nWood, Pulp Paper, Publishing Products\\nNA\\n43\\n114\\n169\\n223\\n116\\n102\\n108\\nMineral Products\\n334\\n553\\n557\\n677\\n694\\n275\\n230\\n243\\ncement mfg\\n318\\n522\\n524\\n618\\n630\\n181\\n147\\n156\\nSOLVENT UTILIZATION\\nNA\\nNA\\nNA\\nNA\\nNA\\n0\\n1\\n1\\nSTORAGE TRANSPORT\\nNA\\nNA\\nNA\\nNA\\nNA\\n7\\n3\\n3\\nWASTE DISPOSAL RECYCLING\\n3\\n3\\n10\\n8\\n33\\n42\\n41\\n42\\nON-ROAD VEHICLES\\n3\\n103\\n114\\n411\\n521\\n542\\n316\\n326\\nLight-Duty Gas Vehicles Motorcycles\\nNA\\nNA\\nNA\\n132\\n159\\n138\\n127\\n130\\nDiesels\\nNA\\nNA\\nNA\\n231\\n303\\n337\\n83\\n85\\nNON-ROAD ENGINES AND VEHICLES\\n3,190\\n2,392\\n321\\n83\\n175\\n916\\n1,016\\n1,084\\nMarine Vessels\\n215\\n215\\n105\\n43\\n117\\n251\\n237\\n261\\nRailroads\\n2,975\\n2,174\\n215\\n36\\n53\\n122\\n111\\n114\\nMISCELLANEOUS\\n545\\n545\\n554\\n110\\n11\\n12\\n17\\n12\\nOther Combustion\\n545\\n545\\n554\\n110\\n11\\n12\\n17\\n12\\nFugitive Dust\\nNA\\nNA\\n0\\n0\\n0\\nTOTAL ALL SOURCES\\n19,952\\n22,357\\n22,227\\n31,161\\n25,905\\n23,660\\n19,121\\n19,647\\nNote(s): NA not available. For several source categories, emissions either prior to or beginning with 1985 are not available at the more detailed\\nlevel but are contained in the more aggregate estimate. Zero values represent less than 500 short tons/year.\\n\u00e2\u0080\u009cOther\u00e2\u0080\u009d categories may contain emissions that could not be accurately allocated to specific source categories.\\nThe 1985 fuel combustion, electric utility category is based on the National Allowance Data Base Version 2.11, Acid Rain Division, U.S.\\nEPA, released March 23,1993. Allocations at the Tier 3 levels are approximations only and are based on the methodology described\\nin section 6.0, paragraph 6.2.1.1.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\n3-12 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0070.jp2"}, "71": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-5. Total National Emissions of Directly Emitted Particulate Matter (PM 10\\n1940 through 1998 (thousand short tons)\\nSource Category\\n1940\\n1950\\n1960\\n1970\\n1980\\n1990\\n1996\\n1998\\nFUEL COMB. ELEC. UTIL.\\n962\\n1,467\\n2,117\\n1,775\\n879\\n295\\n287\\n302\\nCoal\\n954\\n1,439\\n2,092\\n1,680\\n796\\n265\\n264\\n273\\nbituminous\\n573\\n865\\n1,288\\n1,041\\n483\\n188\\n195\\n200\\nFUEL COMB. INDUSTRIAL\\n708\\n604\\n331\\n641\\n679\\n270\\n255\\n245\\nCoal\\n549\\n365\\n146\\n83\\n18\\n84\\n77\\n74\\nOther\\n120\\n160\\n103\\n441\\n571\\n87\\n77\\n74\\nFUEL COMB. OTHER\\n2,338\\n1,674\\n1,113\\n455\\n887\\n631\\n632\\n544\\nResidential Wood\\n1,716\\n1,128\\n850\\n384\\n818\\n501\\n503\\n411\\nCHEMICAL ALLIED PRODUCT MFG\\n330\\n455\\n309\\n235\\n148\\n77\\n63\\n65\\nMETALS PROCESSING\\n1,208\\n1,027\\n1,026\\n1,316\\n622\\n214\\n164\\n171\\nNonferrous Metals Processing\\n588\\n346\\n375\\n593\\n130\\n50\\n35\\n37\\ncopper\\n217\\n105\\n122\\n343\\n32\\n14\\n7\\n7\\nFerrous Metals Processing\\n246\\n427\\n214\\n198\\n322\\n155\\n108\\n112\\nprimary\\n86\\n98\\n51\\n31\\n271\\n128\\n86\\n91\\nPETROLEUM RELATED INDUSTRIES\\n366\\n412\\n689\\n286\\n138\\n55\\n32\\n32\\nOTHER INDUSTRIAL PROCESSES\\n3,996\\n6,954\\n7,211\\n5,832\\n1,846\\n583\\n327\\n339\\nAgriculture, Food, Kindred Products\\n784\\n696\\n691\\n485\\n402\\n73\\n61\\n61\\ncountry elevators\\n299\\n307\\n343\\n257\\n258\\n9\\n6\\n6\\nterminal elevators\\n351\\n258\\n224\\n147\\n86\\n6\\n2\\n2\\nWood, Pulp Paper, Publishing Products\\n511\\n798\\n958\\n727\\n183\\n105\\n78\\n82\\nsulfate (kraft) pulping\\n470\\n729\\n886\\n668\\n142\\n73\\n43\\n45\\nMineral Products\\n2,701\\n5,460\\n5,563\\n4,620\\n1,261\\n367\\n156\\n162\\ncement mfg\\n1,363\\n1,998\\n2,014\\n1,731\\n417\\n190\\n21\\n22\\nstone quarrying/processing\\n482\\n663\\n1,039\\n957\\n421\\n54\\n24\\n24\\nSOLVENT UTILIZATION\\nNA\\nNA\\nNA\\nNA\\nNA\\n4\\n6\\n6\\nSTORAGE TRANSPORT\\nNA\\nNA\\nNA\\nNA\\nNA\\n102\\n90\\n94\\nBulk Materials Storage\\nNA\\nNA\\nNA\\nNA\\nNA\\n100\\n87\\n91\\nWASTE DISPOSAL RECYCLING\\n392\\n505\\n764\\n999\\n273\\n271\\n304\\n310\\nOpen Burning\\n220\\n333\\n544\\n770\\n198\\n206\\n211\\n215\\nresidential\\n220\\n333\\n544\\n770\\n198\\n195\\n194\\n197\\nON-ROAD VEHICLES\\n210\\n314\\n554\\n443\\n397\\n336\\n282\\n257\\nDiesels\\nNA\\n9\\n15\\n136\\n208\\n235\\n177\\n152\\nheavy-duty diesel vehicles\\nNA\\n9\\n15\\n136\\n194\\n224\\n168\\n144\\nNON-ROAD ENGINES AND VEHICLES\\n2,480\\n1,788\\n201\\n220\\n398\\n489\\n457\\n461\\nNon-Road Diesel\\n1\\n16\\n22\\n281\\n439\\n301\\n297\\n301\\nconstruction\\n0\\n12\\n12\\n102\\n148\\n149\\n147\\n150\\nfarm\\n0\\n4\\n7\\n140\\n239\\n78\\n72\\n69\\nRailroads\\n2,464\\n1,742\\n110\\n25\\n37\\n53\\n27\\n27\\nNATURAL SOURCES\\nNA\\nNA\\nNA\\nNA\\nNA\\n2,092\\n5,307\\n5,307\\nGeogenic wind erosion*\\nNA\\nNA\\nNA\\nNA\\nNA\\n2,092\\n5,307\\n5,307\\nMISCELLANEOUS\\n2,968\\n1,934\\n1,244\\n839\\n852\\n24,542\\n24,836\\n26,609\\nAgriculture Forestry\\nNA\\nNA\\nNA\\nNA\\nNA\\n5,292\\n4,905\\n4,970\\nagricultural crops**\\nNA\\nNA\\nNA\\nNA\\nNA\\n4,745\\n4,328\\n4,366\\nagricultural livestock**\\nNA\\nNA\\nNA\\nNA\\nNA\\n547\\n577\\n603\\nOther Combustion\\n2,968\\n1,934\\n1,244\\n839\\n852\\n1,181\\n1,254\\n1,018\\nFugitive Dust\\nNA\\nNA\\nNA\\nNA\\nNA\\n18,069\\n18,675\\n20,619\\nunpaved roads**\\nNA\\nNA\\nNA\\nNA\\nNA\\n11,234\\n12,059\\n12,668\\npaved roads**\\nNA\\nNA\\nNA\\nNA\\nNA\\n2,248\\n2,390\\n2,618\\nconstruction**\\nNA\\nNA\\n4,249\\n3,578\\n4,545\\nTOTAL ALL SOURCES\\n15,957\\n17,133\\n15,558\\n13,042\\n7,119\\n29,962\\n33,041\\n34,741\\nNote(s): N A not available. For several source categories, emissions either prior to or beginning with 1985 are not available at the more detailed\\nlevel but are contained in the more aggregate estimate. Zero values represent less than 500 short tons/year.\\nCategories displayed below Tier 1 do not sum to Tier 1 totals because they are intended to show major contributors.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\nAlthough geogenic wind erosion emissions are included in this summary table, it is very difficult to interpret annual estimates of PM\\nemissions from this source category in a meaningful way, owing to the highly episodic nature of the events that contribute to these\\nemissions.\\nThese are the main source categories of PM crustal material emissions. A report by the Desert Research Institute found that about\\n75% of these emissions are within 2 m of the ground at the point they are measured. Thus, most of them are likely to be removed or\\ndeposited within a few km of their release, depending on atmospheric turbulence, temperature, soil moisture, availability of horizontal\\nand vertical surfaces for impaction and initial suspension energy. This is consistent with the generally small amount of crustal materials\\nfound on speciated ambient samples. (See reference 6 in Chapter 2.)\\n3.0 Summary of National Emissions Trends 3-13", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0071.jp2"}, "72": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\nTable 3-6. Total National Emissions of Directly Emitted Particulate Matter (PM 2 5\\n1990 through 1998 (thousand short tons)\\nSource Category\\n1990\\n1991\\n1992\\n1993\\n1994\\n1995\\n1996\\n1997\\n1998\\nFUEL COMB. ELEC. UTIL.\\n121\\n105\\n106\\n112\\n108\\n107\\n156\\n160\\n165\\nCoal\\n97\\n85\\n87\\n90\\n86\\n86\\n133\\n135\\n138\\nbituminous\\n59\\n53\\n53\\n57\\n54\\n52\\n88\\n89\\n91\\nFUEL COMB. INDUSTRIAL\\n177\\n151\\n159\\n172\\n183\\n203\\n166\\n161\\n160\\nOther\\n73\\n58\\n59\\n69\\n60\\n59\\n62\\n60\\n60\\nFUEL COMB. OTHER\\n611\\n638\\n662\\n568\\n550\\n589\\n537\\n466\\n466\\nResidential Wood\\n501\\n535\\n558\\n464\\n446\\n484\\n433\\n358\\n357\\nCHEMICAL ALLIED PRODUCT MFG\\n47\\n43\\n45\\n41\\n49\\n42\\n38\\n39\\n39\\nMETALS PROCESSING\\n157\\n197\\n198\\n125\\n125\\n134\\n108\\n113\\n112\\nFerrous Metals Processing\\n121\\n89\\n83\\n86\\n86\\n92\\n69\\n72\\n72\\nprimary\\n103\\n72\\n66\\n68\\n68\\n74\\n53\\n56\\n56\\nPETROLEUM RELATED INDUSTRIES\\n27\\n24\\n24\\n22\\n22\\n22\\n18\\n18\\n18\\nOTHER INDUSTRIAL PROCESSES\\n284\\n264\\n259\\n260\\n256\\n256\\n178\\n184\\n187\\nWood, Pulp Paper, Publishing Products\\n77\\n61\\n59\\n59\\n57\\n60\\n54\\n56\\n57\\nMineral Products\\n144\\n134\\n135\\n136\\n133\\n134\\n83\\n87\\n88\\nSOLVENT UTILIZATION\\n4\\n4\\n5\\n6\\n6\\n5\\n5\\n5\\n5\\nSTORAGE TRANSPORT\\n42\\n42\\n50\\n46\\n43\\n42\\n31\\n32\\n32\\nWASTE DISPOSAL RECYCLING\\n234\\n238\\n239\\n288\\n271\\n247\\n234\\n236\\n238\\nOpen Burning\\n187\\n190\\n192\\n195\\n196\\n197\\n186\\n188\\n190\\nresidential\\n177\\n179\\n181\\n183\\n184\\n185\\n176\\n177\\n179\\nON-ROAD VEHICLES\\n275\\n286\\n280\\n257\\n256\\n231\\n221\\n211\\n197\\nDiesels\\n212\\n221\\n216\\n192\\n190\\n169\\n157\\n147\\n134\\nhddv\\n203\\n212\\n206\\n183\\n182\\n161\\n149\\n140\\n127\\nNON-ROAD ENGINES AND VEHICLES\\n432\\n432\\n433\\n427\\n424\\n403\\n410\\n411\\n413\\nNon-Road Diesel\\n277\\n275\\n273\\n273\\n272\\n272\\n274\\n275\\n277\\nconstruction\\n137\\n136\\n136\\n135\\n134\\n134\\n135\\n136\\n138\\nfarm\\n71\\n71\\n70\\n69\\n68\\n67\\n66\\n65\\n63\\nNATURAL SOURCES\\n314\\n312\\n334\\n76\\n324\\n172\\n796\\n796\\n796\\nGeogenic wind erosion*\\n314\\n312\\n334\\n76\\n324\\n172\\n796\\n796\\n796\\nMISCELLANEOUS\\n5,234\\n5,004\\n4,854\\n4,926\\n5,360\\n4,725\\n5,298\\n5,652\\n5,549\\nAgriculture Forestry\\n1,031\\n1,019\\n976\\n887\\n941\\n952\\n952\\n964\\n964\\nagricultural crops*\\n949\\n937\\n893\\n803\\n856\\n867\\n866\\n875\\n873\\nagricultural livestock\\n82\\n83\\n83\\n84\\n85\\n85\\n87\\n90\\n91\\nOther Combustion\\n1,037\\n807\\n666\\n693\\n913\\n734\\n1,040\\n1,150\\n882\\nFugitive Dust\\n3,166\\n3,178\\n3,213\\n3,346\\n3,506\\n3,038\\n3,304\\n3,535\\n3,701\\nunpaved roads\\n1,687\\n1,684\\n1,642\\n1,718\\n1,709\\n1,559\\n1,819\\n1,892\\n1,912\\npaved roads\\n562\\n600\\n606\\n616\\n634\\n585\\n598\\n635\\n655\\nconstruction\\n850\\n818\\n892\\n930\\n1,049\\n777\\n750\\n857\\n968\\nTOTAL ALL SOURCES\\n7,958\\n7,739\\n7,648\\n7,327\\n7,975\\n7,179\\n8,194\\n8,483\\n8,379\\nNote(s): NA not available. Zero values represent less than 500 short tons/year.\\nCategories displayed below Tier 1 do not sum to Tier 1 totals because they are intended to show major contributors.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\nAlthough geogenic wind erosion emissions are included in this summary table, it is very difficult to interpret annual estimates of PM\\nemissions from this source category in a meaningful way, owing to the highly episodic nature of the events that contribute to these\\nemissions.\\nThese are the main source categories of PM crustal material emissions. A report by the Desert Research Institute found that about\\n75% of these emissions are within 2 m of the ground at the point they are measured. Thus, most of them are likely to be removed or\\ndeposited within a few km of their release, depending on atmospheric turbulence, temperature, soil moisture, initial suspension energy\\nand availability of horizontal and vertical surfaces for impaction. This is consistent with the generally small amount of crustal materials\\nfound on speciated ambient samples. (See reference 6 in Chapter 2.)\\nFor a complete understanding of PM 2 5 emissions, one should also consider the emissions of S0 2 NO x and NH 3 These gases react\\nin the atmosphere to form ammonium sulfate and ammonium nitrate fine particles; also, some organic particles are formed from VOCs.\\nThese \u00e2\u0080\u009csecondary\u00e2\u0080\u009d fine particles (in contrast to the directly emitted particles from combustion and fugitive dust) can comprise as much\\nas half the PM 2 5 measured in the United States. 7 Source apportionment studies exist to help elucidate the role of primary PM (reflected\\nin the NET) and secondary PM.\\n3-14 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0072.jp2"}, "73": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-7. Total National Emissions of Lead, 1970 through 1998\\n(short tons)\\nSource Category\\n1970\\n1975\\n1980\\n1985\\n1990\\n1996\\n1998\\nFUEL COMB. ELEC. UTIL.\\n327\\n230\\n129\\n64\\n64\\n61\\n68\\nCoal\\n300\\n189\\n95\\n51\\n46\\n53\\n54\\nbituminous\\n181\\n114\\n57\\n31\\n28\\n32\\n33\\nOil\\n28\\n41\\n34\\n13\\n18\\n8\\n14\\nFUEL COMB. INDUSTRIAL\\n237\\n75\\n60\\n30\\n18\\n16\\n19\\nCoal\\n218\\n60\\n45\\n22\\n14\\n13\\n13\\nbituminous\\n146\\n40\\n31\\n15\\n10\\n9\\n9\\nOil\\n19\\n16\\n14\\n8\\n3\\n3\\n5\\nFUEL COMB. OTHER\\n10,052\\n10,042\\n4,111\\n421\\n418\\n415\\n416\\nMisc. Fuel Comb. (Except Residential)\\n10,000\\n10,000\\n4,080\\n400\\n400\\n400\\n400\\nCHEMICAL ALLIED PRODUCT MFG\\n103\\n120\\n104\\n118\\n136\\n167\\n175\\nInorganic Chemical Mfg\\n103\\n120\\n104\\n118\\n136\\n167\\n175\\nlead oxide and pigments\\n103\\n120\\n104\\n118\\n136\\n167\\n175\\nMETALS PROCESSING\\n24,224\\n9,923\\n3,026\\n2,097\\n2,170\\n2,055\\n2,098\\nNonferrous Metals Processing\\n15,869\\n7,192\\n1,826\\n1,376\\n1,409\\n1,333\\n1,371\\nprimary lead production\\n12,134\\n5,640\\n1,075\\n874\\n728\\n588\\n628\\nprimary copper production\\n242\\n171\\n20\\n19\\n19\\n22\\n23\\nprimary zinc production\\n1,019\\n224\\n24\\n16\\n9\\n13\\n13\\nsecondary lead production\\n1,894\\n821\\n481\\n288\\n449\\n514\\n505\\nsecondary copper production\\n374\\n200\\n116\\n70\\n75\\n76\\n83\\nlead battery manufacture\\n41\\n49\\n50\\n65\\n78\\n103\\n117\\nlead cable coating\\n127\\n55\\n37\\n43\\n50\\n16\\n1\\nFerrous Metals Processing\\n7,395\\n2,196\\n911\\n577\\n576\\n529\\n542\\ncoke manufacturing\\n11\\n8\\n6\\n3\\n4\\n0\\n0\\nferroalloy production\\n219\\n104\\n13\\n7\\n18\\n8\\n4\\niron production\\n266\\n93\\n38\\n21\\n18\\n18\\n19\\nsteel production\\n3,125\\n1,082\\n481\\n209\\n138\\n160\\n173\\ngray iron production\\n3,773\\n910\\n373\\n336\\n397\\n343\\n345\\nMetals Processing NEC\\n960\\n535\\n289\\n144\\n185\\n193\\n186\\nmetal mining\\n353\\n268\\n207\\n141\\n184\\n192\\n186\\nOTHER INDUSTRIAL PROCESSES\\n2,028\\n1,337\\n808\\n316\\n169\\n51\\n54\\nMineral Products\\n540\\n217\\n93\\n43\\n26\\n29\\n31\\ncement manufacturing\\n540\\n217\\n93\\n43\\n26\\n29\\n31\\nMiscellaneous Industrial Processes\\n1,488\\n1,120\\n715\\n273\\n143\\n22\\n23\\nWASTE DISPOSAL RECYCLING\\n2,200\\n1,595\\n1,210\\n871\\n804\\n609\\n620\\nIncineration\\n2,200\\n1,595\\n1,210\\n871\\n804\\n609\\n620\\nmunicipal waste\\n581\\n396\\n161\\n79\\n67\\n76\\n75\\nother\\n1,619\\n1,199\\n1,049\\n792\\n738\\n534\\n546\\nON-ROAD VEHICLES\\n171,961\\n130,206\\n60,501\\n18,052\\n421\\n19\\n19\\nLight-Duty Gas Vehicles Motorcycles\\n142,918\\n106,868\\n47,184\\n13,637\\n314\\n12\\n12\\nLight-Duty Gas Trucks\\n22,683\\n19,440\\n11,671\\n4,061\\n100\\n7\\n7\\nHeavy-Duty Gas Vehicles\\n6,361\\n3,898\\n1,646\\n354\\n7\\n0\\n0\\nNON-ROAD ENGINES AND VEHICLES\\n9,737\\n6,130\\n4,205\\n921\\n776\\n505\\n503\\nNon-Road Gasoline\\n8,340\\n5,012\\n3,320\\n229\\n158\\n0\\n0\\nAircraft\\n1,397\\n1,118\\n885\\n692\\n619\\n505\\n503\\nTOTAL ALL SOURCES\\n220,869\\n159,659\\n74,153\\n22,890\\n4,975\\n3,899\\n3,973\\nNote(s): N A not available. For several source categories, emissions either prior to or beginning with 1985 are not available at the more detailed\\nlevel but are contained in the more aggregate estimate. Zero values represent less than 500 short tons/year.\\nCategories displayed below Tier 1 do not sum to Tier 1 totals because they are intended to show major contributors.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\n3.0 Summary of National Emissions Trends 3-15", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0073.jp2"}, "74": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\nTable 3-8. Total National Emissions of Ammonia, 1990 through 1998\\n(thousand short tons)\\nSource Category\\n1990\\n1991\\n1992\\n1993\\n1994\\n1995\\n1996\\n1997\\n1998\\nFUEL COMB. ELEC. UTIL.\\n0\\n0\\n0\\n0\\n0\\n0\\n6\\n7\\n8\\nFUEL COMB. INDUSTRIAL\\n17\\n17\\n17\\n18\\n18\\n18\\n49\\n48\\n47\\nFUEL COMB. OTHER\\n8\\n8\\n8\\n8\\n8\\n8\\n7\\n7\\n6\\nCHEMICAL ALLIED PRODUCT MFG\\n183\\n183\\n183\\n183\\n183\\n183\\n158\\n160\\n165\\nMETALS PROCESSING\\n6\\n6\\n6\\n6\\n6\\n6\\n5\\n5\\n5\\nPETROLEUM RELATED INDUSTRIES\\n43\\n43\\n43\\n43\\n43\\n43\\n34\\n35\\n35\\nOTHER INDUSTRIAL PROCESSES\\n38\\n38\\n39\\n39\\n40\\n40\\n43\\n44\\n44\\nSOLVENT UTILIZATION\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nSTORAGE TRANSPORT\\n0\\n0\\n0\\n0\\n0\\n0\\n1\\n1\\n1\\nWASTE DISPOSAL RECYCLING\\n82\\n86\\n89\\n93\\n93\\n93\\n84\\n84\\n86\\nON-ROAD VEHICLES\\n192\\n205\\n217\\n227\\n239\\n259\\n231\\n240\\n250\\nNON-ROAD ENGINES AND VEHICLES\\n6\\n7\\n7\\n7\\n7\\n7\\n9\\n10\\n10\\nNATURAL SOURCES\\n30\\n29\\n28\\n29\\n30\\n31\\n32\\n33\\n34\\nBiogenic\\n30\\n29\\n28\\n29\\n30\\n31\\n32\\n33\\n34\\nMISCELLANEOUS\\n3,727\\n3,770\\n3,814\\n3,869\\n3,924\\n3,979\\n4,113\\n4,163\\n4,244\\nAgriculture Forestry\\n3,727\\n3,770\\n3,814\\n3,869\\n3,924\\n3,979\\n4,113\\n4,163\\n4,244\\nlivestock agriculture\\n3,307\\n3,324\\n3,341\\n3,370\\n3,399\\n3,427\\n3,456\\n3,485\\n3,520\\nfertilizer application\\n420\\n446\\n473\\n499\\n525\\n551\\n657\\n678\\n724\\nTOTAL ALL SOURCES\\n4,331\\n4,390\\n4,449\\n4,521\\n4,589\\n4,665\\n4,772\\n4,837\\n4,935\\nNote(s): NA not available. Zero values represent less than 500 short tons/year.\\nCategories displayed below Tier 1 do not sum to Tier 1 totals because they are intended to show major contributors.\\nIn order to convert emissions to gigagrams (thousand metric tons), multiply the above values by 0.9072.\\n3-16 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0074.jp2"}, "75": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-9. Carbon Monoxide Federal Emission Standards, 1970 to 1991\\nEmission Limit\\n(grams of CO per mile)\\nModel year\\nLight-duty Vehicles\\nLight-duty Trucks\\n(0 to 6,000 lbs.)\\n1970-1971\\n23\\n1972-1974\\n39\\n39\\n1975-1979\\n15\\n20 1\\n1980-1991\\n3.4 2\\n18 3 10 4\\nNote(s): 1 Standard applies for 1975-1978 model years.\\n2 Certain vehicles were subject to a less stringent requirement of 7.0 grams\\nper mile from model years 1980-1984.\\n3 Standard applies for 1979-1983 model years.\\n4 Standard applies for 1984-1991 model years.\\nThe first vehicle standards were implemented by the Federal government in 1968 and were\\nconcentration based (ppm of exhaust for hydrocarbons and CO). The first mass based\\nstandards (g/mile) were in 1972.\\nTable 3-10. Nitrogen Oxide and Volatile Organic Compound Federal\\nEmission Limits for Light-Duty Vehicles, 1972 to 1991\\nEmission Limit\\n(grams per mile)\\nModel Year\\nNO x\\nVOC 1\\n1972-1974\\n3.0 2\\n3.4\\n1975-1979\\n3.1 3 2.0 4\\n1.5\\n1980-1991\\n1 0 5\\n0.41\\nNote(s): 1 These are exhaust emission standards for VOC.\\n2 Standard applies for 1973-1974 model years.\\nStandard applies for 1975-1976 model years.\\n4 Standard applies for 1977-1980 model years.\\n5 Standard applies for 1981 -1991 model years.\\nThe first vehicle standards were implemented by the Federal government in 1968 and were\\nconcentration based (ppm of exhaust for hydrocarbons and CO). The first mass based\\nstandards (g/mile) were in 1972.\\n3.0 Summary of National Emissions Trends 3-17", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0075.jp2"}, "76": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-11. Nitrogen Oxide and Volatile Organic Compound Federal\\nEmission Limits for Light-Duty Trucks, 1972 to 1991\\nEmission Limit\\n(grams per mile)\\nModel Year\\nNO x\\nVOC 1\\n1972-1974\\n3.0 2\\n3.4\\n1975-1978\\n3.1 3\\n2.0\\n1979-1984\\nCO\\nc\\\\i\\n1.7\\n1985-1991\\n1.2 5,6\\n0.8\\nNote(s): 1\\n2\\n3\\n4\\n5\\n6\\nThese are exhaust emission standards for VOC.\\nStandard applies for 1973-1974 model years.\\nStandard applies for 1975-1978 model years.\\nStandard applies for 1979-1987 model years.\\nStandard applies for 1988-1993 model years.\\nLight-duty trucks with a loaded-vehicle weight more than 3,750 pounds are\\nsubject to a 1.7 grams per mile standard for these model years.\\nThe first vehicle standards were implemented by the Federal government in 1968 and\\nwere concentration based (ppm of exhaust for hydrocarbons and CO). The first mass\\nbased standards (g/mile) were in 1972.\\nTable 3-12. Federal Test Procedure Exhaust Emissions Standards and Schedule\\nfor Light-Duty Vehicles and Light-Duty Trucks, 1992 to 1998\\nVehicle Useful Life (grams/mile)\\n5 Years/50,100 Miles 10 Years/100,100 Miles 1\\nVehicle Emission\\nType\\nCategory\\nYear 2\\nTHC 3\\nNMHC 4\\nCO\\nNO x\\nPM 10\\nTHC\\nNMHC\\nCO\\nNO x\\nPM 10\\nLDV\\nTier 0\\n1992\\n0.41\\n0.34\\n3.4\\n1.0\\n0.20\\nLDV\\nTier 1\\n1996\\n0.41\\n0.25\\n3.4\\n0.4\\n0.08\\n0.31\\n4.2\\n0.6\\n0.10\\nLDGTIa 5\\nTier 0\\n1992\\n0.80\\n0.67\\n10\\n1.2\\n0.26\\nLDGTIa\\nTier 1\\n1996\\n0.25\\n3.4\\n0.4\\n0.08\\n0.80\\n0.31\\n4.2\\n0.6\\n0.10\\nLDGTIb 6\\nTier 0\\n1992\\n0.80\\n0.67\\n10\\n1.7\\n0.13\\nLDGTIb\\nTier 1\\n1996\\n0.32\\n4.4\\n0.7\\n0.08\\n0.80\\n0.40\\n5.5\\n0.97\\n0.10\\nLDGT2a 7\\nTier 0\\n1992\\n0.80\\n0.67\\n10\\n1.7\\n0.26\\nLDGT2a\\nTier 1\\n1997\\n0.32\\n4.4\\n0.7\\n0.80\\n0.46\\n6.4\\n1.0\\n0.10\\nLDGT2b 8\\nTier 0\\n1992\\n0.80\\n0.67\\n10\\n1.7\\n0.13\\nLDGT2b\\nTier 1\\n1997\\n0.39\\n5.0\\n1.1\\n0.80\\n0.56\\n7.3\\n1.53\\n0.12\\nNotes:\\n1 LDGT2: 11 years/120,000 miles\\n2 Year Standard is 100 percent of vehicles affected\\n3 Total hydrocarbons\\n4 Nonmethane Hydrocarbon\\n5 Any light light-duty truck up through 3,750 lbs loaded vehicle weight.\\n6 Any light light-duty truck greater than 3,750 lbs loaded vehicle weight.\\n7 Any heavy light-duty truck up through 5,750 lbs adjusted loaded vehicle weight.\\n8 Any heavy light-duty truck greater than 5,750 lbs adjusted loaded vehicle weight.\\nThe first vehicle standards were implemented by the Federal government in 1968 and were concentration based (ppm of exhaust for\\nhydrocarbons and CO). The first mass based standards (g/mile) were in 1972.\\nSource: U.S. EPA Office of Mobile Sources, EPA-420-B-98-001\\n3-18 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0076.jp2"}, "77": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-13. Total National Emissions by Pollutant and Year\\nYear\\nCO\\nNO x\\nvoc\\nS0 2\\nPM 10\\npm 25\\nPb\\nnh 3\\n1940\\n93,616\\n7,374\\n17,161\\n19,952\\n15,957\\n1941\\n91,657\\n8,262\\n17,235\\n22,857\\n16,074\\n1942\\n92,449\\n8,389\\n16,358\\n24,541\\n16,192\\n1943\\n93,241\\n8,972\\n16,323\\n26,846\\n16,309\\n1944\\n94,033\\n9,455\\n16,539\\n27,092\\n16,427\\n1945\\n94,825\\n9,548\\n17,308\\n26,007\\n16,545\\n1946\\n95,617\\n9,993\\n20,549\\n23,297\\n16,663\\n1947\\n96,409\\n10,470\\n19,507\\n26,298\\n16,780\\n1948\\n97,202\\n9,985\\n19,349\\n24,284\\n16,898\\n1949\\n97,993\\n10,247\\n19,720\\n20,801\\n17,016\\n1950\\n102,609\\n10,093\\n20,936\\n22,357\\n17,133\\n1951\\n99,285\\n10,535\\n20,398\\n21,477\\n16,976\\n1952\\n99,784\\n11,056\\n20,208\\n20,826\\n16,818\\n1953\\n100,283\\n11,104\\n21,258\\n20,920\\n16,661\\n1954\\n100,782\\n11,663\\n21,232\\n20,181\\n16,503\\n1955\\n101,281\\n11,563\\n21,973\\n20,883\\n16,345\\n1956\\n101,780\\n11,867\\n22,902\\n21,039\\n16,188\\n1957\\n102,279\\n12,248\\n22,784\\n21,272\\n16,031\\n1958\\n102,778\\n13,012\\n21,846\\n22,634\\n15,873\\n1959\\n103,278\\n13,486\\n22,703\\n22,654\\n15,715\\n1960\\n109,745\\n14,140\\n24,459\\n22,227\\n15,558\\n1961\\n106,207\\n13,809\\n24,584\\n22,142\\n15,286\\n1962\\n108,637\\n14,408\\n25,036\\n22,955\\n15,014\\n1963\\n111,067\\n15,100\\n27,062\\n24,133\\n14,742\\n1964\\n113,498\\n15,871\\n26,948\\n25,301\\n14,470\\n1965\\n115,928\\n16,579\\n27,630\\n26,750\\n14,198\\n1966\\n118,358\\n17,390\\n27,827\\n28,849\\n13,926\\n1967\\n120,788\\n17,635\\n28,209\\n28,493\\n13,654\\n1968\\n123,219\\n18,372\\n26,568\\n30,263\\n13,382\\n1969\\n125,649\\n18,847\\n26,764\\n30,961\\n13,110\\n1970\\n129,444\\n20,928\\n30,982\\n31,161\\n13,042\\n220,869\\n1971\\n129,491\\n21,559\\n30,039\\n29,686\\n11,335\\n243,415\\n1972\\n128,779\\n22,740\\n30,297\\n30,390\\n10,734\\n255,555\\n1973\\n125,935\\n23,529\\n29,873\\n31,754\\n10,237\\n223,686\\n1974\\n119,978\\n22,915\\n28,042\\n30,032\\n9,636\\n178,693\\n1975\\n116,757\\n22,632\\n26,079\\n28,011\\n7,671\\n159,659\\n1976\\n120,963\\n24,051\\n26,991\\n28,435\\n7,906\\n165,349\\n1977\\n120,868\\n24,808\\n27,426\\n28,623\\n7,739\\n152,467\\n1978\\n122,150\\n25,070\\n27,655\\n26,877\\n7,865\\n137,964\\n1979\\n118,475\\n24,716\\n27,161\\n26,941\\n7,571\\n116,786\\n1980\\n117,434\\n24,384\\n26,336\\n25,905\\n7,119\\n74,153\\n1981\\n114,396\\n24,211\\n24,956\\n24,612\\n6,605\\n58,884\\n1982\\n112,260\\n23,785\\n23,866\\n23,319\\n5,274\\n57,666\\n1983\\n117,675\\n23,639\\n25,078\\n22,807\\n6,021\\n49,232\\n1984\\n116,533\\n24,322\\n26,015\\n23,816\\n6,281\\n42,217\\n1985\\n117,013\\n23,198\\n24,428\\n23,658\\n45,445\\n22,890\\n1986\\n111,688\\n22,808\\n23,617\\n22,892\\n51,137\\n7,296\\n1987\\n110,798\\n23,068\\n23,470\\n22,675\\n42,533\\n6,840\\n1988\\n118,729\\n24,124\\n24,306\\n23,135\\n61,072\\n7,053\\n1989\\n106,439\\n23,893\\n22,513\\n23,293\\n53,064\\n5,468\\n3.0 Summary of National Emissions Trends 3-19", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0077.jp2"}, "78": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 3-13 (continued)\\nYear\\nCO\\nNO x\\nvoc\\nS0 2\\nPM 10\\npm 25\\nPb\\nnh 3\\n1990\\n98,523\\n24,049\\n20,936\\n23,660\\n29,962\\n7,958\\n4,975\\n4,331\\n1991\\n100,872\\n24,249\\n21,102\\n23,041\\n29,560\\n7,739\\n4,169\\n4,390\\n1992\\n97,630\\n24,596\\n20,659\\n22,806\\n29,472\\n7,648\\n3,810\\n4,449\\n1993\\n98,160\\n24,961\\n20,868\\n22,466\\n28,006\\n7,327\\n3,916\\n4,521\\n1994\\n102,643\\n25,372\\n21,535\\n21,870\\n30,913\\n7,975\\n4,047\\n4,589\\n1995\\n93,353\\n24,921\\n20,817\\n19,181\\n27,070\\n7,179\\n3,929\\n4,665\\n1996\\n95,479\\n24,676\\n18,736\\n19,121\\n33,041\\n8,194\\n3,899\\n4,772\\n1997\\n94,410\\n24,824\\n18,876\\n19,622\\n34,226\\n8,483\\n3,952\\n4,837\\n1998\\n89,454\\n24,454\\n17,917\\n19,647\\n34,741\\n8,379\\n3,973\\n4,935\\n3-20 3.0 Summary of National Emissions Trends", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0078.jp2"}, "79": {"fulltext": "Figure 3-1. Trend in Gross Domestic Product, Population, Vehicle Miles\\nTraveled, Total Fuel Consumption, combined VOLATILE ORGANIC\\nCOMPOUND and NITROGEN OXIDES Emissions, and SULFUR DIOXIDE\\nEmissions, 1970 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\nm o in m\\nCM CM T-\\n0Z6L o* pexapui\\n3.0 Summary of National Emissions Trends 3-21\\n1970 1972 1974 1976 1978 1980 1982 1984 1986 1988 1990 1992 1994 1996 1998", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0079.jp2"}, "80": {"fulltext": "Figure 3-2. Trend in CARBON MONOXIDE Emissions,\\n1940 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\n(suo; jjoqs uojnjuj) suojssjuig\\n3-22 3.0 Summary of National Emissions Trends\\nNote: Some fluctuations in the years before 1970 are the result of different methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0080.jp2"}, "81": {"fulltext": "Figure 3-3. Trend in NITROGEN OXIDE Emissions,\\n1940 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\n(suoj vioqs uojujiu) suo;ss;iug\\nin\\no\\no\\nm\\n00\\no\\noo\\no\\nm\\nh-\\no\\nin\\nco\\no\\nin\\nm\\no\\nm\\nO)\\n3.0 Summary of National Emissions Trends 3-23\\nNote: Some fluctuations in the years before 1970 are the result of different methodologies", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0081.jp2"}, "82": {"fulltext": "Figure 3-4. Trend in VOLATILE ORGANIC COMPOUND\\nEmissions, 1940 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\no\\n3\\nD\\nE\\no\\no\\no\\n3-24 3.0 Summary of National Emission Trends\\nYear\\nFuel Combustion Industrial Processing Solvent Utilization On-road\\nNon-road Miscellaneous", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0082.jp2"}, "83": {"fulltext": "Figure 3-5. Trend in SULFUR DIOXIDE Emissions, 1940 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\n(suo) jjoijs uojHjiu) suojssjiug\\nLO\\no\\no\\no\\no\\n10\\n00\\na\\nLO\\nh-\\no\\nLO\\nCO\\nO)\\nLO\\nLO\\nJ)\\nLO\\no\\n3.0 Summary of National Emissions Trends 3-25\\nNote: Some fluctuations in the years before 1970 are the result of different methodologies", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0083.jp2"}, "84": {"fulltext": "Figure 3-6. Trend in PARTICULATE MATTER (PM 10\\nEmissions Excluding Fugitive Dust Sources, 1940 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\nOOCOTj-CNOCOCOTtCMO\\n(suoj }joijs uojHjui) suojssjtug\\n3-26 *3.0 Summary of National Emission Trends\\n1940 1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0084.jp2"}, "85": {"fulltext": "Figure 3-7. Trend in Directly Emitted PARTICULATE MATTER (PM 2 5\\nEmissions Excluding Fugitive Dust Sources, 1990 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\n(SUO} }JOl|S UOjlljUj) SUOjSSjlUg\\n(Q\\n0\\n3.0 Summary of National Emissions Trends 3-27\\nFuel Combustion Industrial Processing On-road Non-road Miscellaneous", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0085.jp2"}, "86": {"fulltext": "Figure 3-8. Trend in LEAD Emissions,\\n1970 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\nCO CM CM t- t-\\n(suoj jjoqs uojiijiu) suojssiuig\\n0\\no\\n3-28 3.0 Summary of National Emission Trends\\nFuel Combustion Industrial Processing On-road Non-road Miscellaneous", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0086.jp2"}, "87": {"fulltext": "Figure 3-9. Trend in AMMONIA Emissions,\\n1990 to 1998\\nNational Air Pollutant Emission Trends, 1990-1998\\n00\\n(suo; jjoijs uo;i|jUj) suofssjiug\\n3.0 Summary of National Emissions Trends 3-29", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0087.jp2"}, "88": {"fulltext": "[This page intentionally left blank.]", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0088.jp2"}, "89": {"fulltext": "Chapter 4.0 Section 406 of the Clean Air Act\\nAmendments: Industrial S0 2\\nEmissions\\nThis chapter discusses the impact of industrial sulfur\\ndioxide (S0 2 emissions, the source categories comprising\\nindustrial emissions, base year emissions development,\\nprojected emissions methodology, long-term emission trends,\\nand desulfurization of diesel fuel benefits.\\n4.1 WHY A SEPARATE CHAPTER FOR\\nINDUSTRIAL S0 2 EMISSIONS?\\nThe major health effects associated with high exposures\\nto S0 2 in the ambient air include problems in breathing,\\nrespiratory illness, alterations in the lung\u00e2\u0080\u0099s defenses, and\\naggravation of existing respiratory and cardiovascular disease.\\nPeople most sensitive to S0 2 include asthmatics and\\nindividuals with chronic lung disease (such as bronchitis or\\nemphysema) or cardiovascular disease. Children and the\\nelderly may also be sensitive.\\nS0 2 also produces foliar damage on trees and agricultural\\ncrops. S0 2 and nitrogen oxides (NO x in the air cause acidic\\ndeposition, commonly known as acid rain. Acid rain is\\nassociated with a number of effects including acidification of\\nlakes and streams, damage to high-elevation forests, and\\naccelerated corrosion of buildings and monuments. S0 2 and\\nNO x emissions also form sulfates and nitrates in the\\natmosphere that can significantly impair visibility.\\nThis chapter provides information required under section\\n406 of the Clean Air Act Amendments (CAAA) of 1990 (42\\nU.S.C. 7651 note), which deals with S0 2 emissions from\\nindustrial sources. Section 406(a) states that:\\nNot later than January 1, 1995 and every 5 years\\nthereafter, the Administrator of the Environmental\\nProtection Agency shall transmit to the Congress a\\nreport containing an inventory of national annual\\nsulfur dioxide emissions from industrial sources (as\\ndefined in title IV of the Act), including units subject\\nto section 405(g)(6) of the Clean Air Act, for all\\nyears for which data are available, as well as the\\nlikely trend in such emissions over the following 20-\\nyear period. The reports shall also contain estimates\\nof the actual emission reduction in each year\\nresulting from promulgation of the diesel fuel\\ndesulfurization regulations under section 214.\\nAs discussed below, the United States (U.S.) Environmental\\nProtection Agency (EPA) intends this chapter to provide the\\ninformation required in section 406(a).\\n4.1.1 What Source Categories Are Industrial\\nSources?\\nSeveral provisions of the CAA and the CAAA address\\nwhat source categories are industrial sources. Section 402(24)\\nof the CAA defines industrial sources. An industrial source is:\\na unit that does not serve a generator that produces\\nelectricity, a \u00e2\u0080\u009cnonutility unit\u00e2\u0080\u009d as defined in this\\nsection, or a process source as defined in section\\n410(e).\\nFurther, section 406(a) of the CAAA of 1990 states that\\n\u00e2\u0080\u009cindustrial sources\u00e2\u0080\u009d include units subject to section 405(g)(6)\\nof the CAA. (EPA believes that the reference in section\\n406(b) to section 405(g)(5) is erroneous and reads if as\\nreferring to section 405(g)(6).) Section 405(g)(6) of the CAA\\nexcludes from the Acid Rain Program under Title IV of the\\nCAA certain \u00e2\u0080\u009cqualifying small power production facilities],\u00e2\u0080\u009d\\n\u00e2\u0080\u009cqualifying cogeneration facilities],\u00e2\u0080\u009d and \u00e2\u0080\u009cindependent power\\nproduction facilities].\u00e2\u0080\u009d\\nIn order to determine the scope of the term \u00e2\u0080\u009cindustrial\\nsource,\u00e2\u0080\u009d it is necessary to consider several other statutory and\\nregulatory definitions and provisions. Section 402(15) of the\\nCAA defines \u00e2\u0080\u009cunit\u00e2\u0080\u009d as a \u00e2\u0080\u009cfossil fuel-fired combustion device.\u00e2\u0080\u009d\\nSection 72.2 of the regulations implementing Title IV of the\\nCAA defines \u00e2\u0080\u009cfossil-fuel fired\u00e2\u0080\u009d as combusting \u00e2\u0080\u009cfossil fuel or\\nany derivative of fossil fuel alone or in combination with any\\nother fuel, independent of the percentage of fossil fuel\\nconsumed in any calendar year.\u00e2\u0080\u009d Section 402(17)(A) of the\\nCAA provides that a \u00e2\u0080\u009cutility unit\u00e2\u0080\u009d is, with certain exceptions\\n(e.g., for certain cogeneration units under section 402(17)(C)),\\nany unit that \u00e2\u0080\u009cserves a generator in any State that produces\\nSection 406 of the CAAA: Industrial SO-, Emissions 4-1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0089.jp2"}, "90": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nelectricity for sale\u00e2\u0080\u009d or that, \u00e2\u0080\u009cduring 1985, served a generator\\nin any State that produced electricity for sale.\u00e2\u0080\u009d\\nThe categories of \u00e2\u0080\u009cindustrial sources\u00e2\u0080\u009d referred to in\\nsection 406(a) of the CAAA of 1990 must be considered in\\nlight of these definitions and provisions. With regard to the\\ncategory of \u00e2\u0080\u009cnonutility units,\u00e2\u0080\u009d section 402(25) of the CAA\\ndefines a \u00e2\u0080\u009cnonutility unit\u00e2\u0080\u009d as \u00e2\u0080\u009ca unit other than a utility unit.\u00e2\u0080\u009d\\nThis category comprises all stationary combustion devices that\\nburn any fossil fuel and that are not affected units under the\\nAcid Rain Program in Title IV of the CAA. Because the\\ndefinition of this category excludes units that are utility units\\nand, except for nonutility units that opt into the Acid Rain\\nProgram under section 410 of the CAA, only utility units are\\naffected units, the category does not generally include any\\naffected units.\\nFor similar reasons, the next category of industrial\\nsources, i.e., \u00e2\u0080\u009cunits that do not serve a generator that produces\\nelectricity,\u00e2\u0080\u009d excludes all utility units and thus generally\\nexcludes all affected units under the Acid Rain Program in\\nTitle IV of the CAA. However, there are some units that are\\nnot affected units under the Acid Rain Program (e.g., units in\\nAlaska and Hawaii and certain cogeneration units under\\nsection 402( 17)(C)) but that do serve a generator that produces\\nelectricity. Therefore, this category of industrial sources is\\nsmaller than the \u00e2\u0080\u009cnonutility unit\u00e2\u0080\u009d category and excludes some\\nstationary fossil-fuel fired combustion devices that are not\\naffected units.\\nAnother category of industrial sources (i.e., \u00e2\u0080\u009cprocess\\nsources\u00e2\u0080\u009d) is not defined in Title IV of the CAA. Section\\n410(d) refers to \u00e2\u0080\u009cprocess sources\u00e2\u0080\u009d but does not define the\\nterm. For the purposes of this chapter, a process source is any\\nsource that emits S0 2 as the result of a production or\\nmanufacturing process and not as the result of any type of fuel\\ncombustion.\\nThe last category of industrial sources comprises units\\nthat are utility units but that are exempt from the Acid Rain\\nProgram under section 405(g)(6) of the CAA. This includes\\ncertain \u00e2\u0080\u009cqualifying small power production facilities\u00e2\u0080\u009d or\\n\u00e2\u0080\u009cqualifying cogeneration facilities\u00e2\u0080\u009d under section 3(17)(C) or\\n3(18)(B) of the Federal Power Act and certain \u00e2\u0080\u009cindependent\\npower production facilities\u00e2\u0080\u009d under section 416(a)(2)(A), (B),\\nand (D) of the CAA. These terms are defined in section 72.2\\nof the regulations implementing the Acid Rain Program.\\nFinally, for purposes of applying the 5.60 million ton\\nannual cap for S0 2 emissions from industrial sources, which\\nis specified in section 406(b) of the CAAA of 1990,\\ncommercial/institutional/residential sources are excluded.\\nThis is because the 5.60 million ton cap was developed using\\nemissions in the 1985 National Acid Precipitation Assessment\\nProgram NAPAP 1 inventory that cover sources involving\\nindustrial combustion and industrial/manufacturing processes\\nand do not cover commercial/institutional/residential sources.\\nCommercial/institutional/residential sources encompass\\ncombustion sources, such as those located at hospitals,\\nuniversities, or residences, that are not related to the\\nproduction of physical products.\\nIn summary, industrial sources covered by the 5.60\\nmillion ton annual cap include: all stationary fossil-fuel fired\\ncombustion devices, except for affected utility units under the\\nAcid Rain Program and except for commercial/institutional/\\nresidential sources; and all process sources.\\nTable 4.1 presents the source categories defined as\\nindustrial sources.\\n4.2 WHY USE 1996 AS THE BASE YEAR?\\nSection 406 of the CAAA of 1990 specifies a 5.60\\nmillion ton cap on S0 2 emissions from industrial sources.\\nCongress derived the cap from industrial source emission\\nestimates developed as part of the 1985 NAPAP inventory.\\nThe 1990 National Emission Trends inventory (now called the\\n\u00e2\u0080\u009cNET inventory\u00e2\u0080\u009d), developed from the 1985 NAPAP\\ninventory, served as the baseline for the previous industrial\\nSO, emission projections presented in the report \u00e2\u0080\u009cNational\\nAnnual Industrial Sulfur Dioxide Emission Trends, 1995-\\n2015: Report to Congress.\u00e2\u0080\u009d 2 Since that report, EPA, along\\nwith State and .local agencies, revised the emission inventory\\nfor two separate time periods for different purposes. The most\\nrecent effort by EPA was the incorporation of 1996 Periodic\\nEmission Inventories (PEI) into the NET inventory. (Refer to\\nSection 5.6 for discussions on the PEI).\\nSince the 1996 NET inventory contains the most recent\\ncomprehensive emissions inventory, EPA chose it for the\\nbaseline for the industrial S0 2 emission estimates in this\\nchapter. Table 4.2 presents the source of base year data for\\neach of the 48 contiguous States. Thirty states provided 1996\\npoint source emission inventories to the EPA, and 12 states\\nprovided acceptable 1996 area source emission inventories.\\nThe emissions for Oregon are from the Grand Canyon\\nVisibility Transport Commission (GCVTC) 1990 inventory.\\nThe point source emissions for 7 other States and the area\\nsource emissions for 16 other States are estimated from the\\nOzone Transport Assessment Group (OTAG) 1990 inventory.\\nThe emission estimates for Alaska and Hawaii point sources\\nare from multi-year Aerometric Information Retrieval System/\\nAIRS Facility Subsystem (AIRS/AFS) retrievals, and EPA has\\nnever sent these estimates to these States for review. EPA\\nestimated the area source emissions for Alaska and Hawaii.\\nThe remaining emissions are from the 1985 NAPAP\\ninventory.\\nFor States that did not provide EPA with a 1996 complete\\ninventory, EPA estimated their emissions for 1996 using\\nBureau of Economic Analysis (BEA) growth factors. EPA did\\nnot assume any new controls nor plant retirements for these\\nsources. More details on the methodology to estimate 1985 to\\n1996 emissions can be found in the NET inventory procedures\\ndocument. 3\\nFigure 4.1 presents the S0 2 industrial source emissions by\\nmajor source categories for the year 1996. Fuel combustion\\n4-2 4.0 Section 406 of the CAAA: Industrial S0 2 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0090.jp2"}, "91": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nsources are the largest contributors to industrial SO,\\nemissions.\\n4.3 HOW DID EPA PROJECT EMISSIONS?\\nIn addition to a national inventory of SO, emissions,\\nsection 406 of the CAAA of 1990 also calls for presentation\\nof the likely trend in such emissions over the following 20-\\nyear period. Thus, Congress requires EPA to estimate future\\nindustrial source SO, emissions under section 406. Although\\nsection 406 calls for development of the likely trend in\\nemission for a 20-year period, EPA developed emission\\nestimates from 1996 (the base year) to 2020 since 2020\\nrepresents 20 years from the completion date of this report.\\nEPA considered fuel switching, energy efficiency (the\\namount of energy saved from the use of more efficient\\nprocesses through time), and economic growth in the\\ndevelopment of these projections. In general, less fuel will be\\nneeded to provide the same amount of energy (in the form of\\nsteam) to an industrial process and the amount of energy\\nneeded per unit output will also decrease as processes become\\nmore efficient. Fuel switching and energy efficiency are\\nreflected in energy correction factors based on information\\nobtained from the U.S. Department of Energy (DOE)\\npublication Annual Energy Outlook 1997. Economic growth\\nfactors were derived from the 1995 BEA Gross State Product\\n(GSP) projections by 2-digit Standard Industrial Classification\\n(SIC) code. These were applied to estimate changes in\\nactivity between 1996 and 2030. 4 For the purposes of\\nsatisfying section 406 requirements, a value was needed on\\n3-year intervals through 2020. Therefore, projections were\\ncalculated by applying growth ratios among existing sources\\nto their base year emissions (1996). Interpolated factors were\\nthen applied to these same categories to estimate the every\\n3-year trend.\\nFurther analysis of the 20-year projection is currently\\nunderway at EPA and results will be reported in the next\\nTrends Report (planned for January 2001 publication).\\n4.4 WHAT IS THE TREND IN INDUSTRIAL\\nS0 2 EMISSIONS?\\nFigure 4.2 presents the estimated trends in industrial\\nsource S0 2 emissions from 1900 to 2020. Table 4.3 presents\\nthe emissions by source category for every 3 years starting\\nwith 1996. The year 2007 is also displayed. The\\nsubcategories for solvent utilization and storage and transport\\nare not displayed since these emissions are very small.\\nThe emission estimates for the base year 1996 are 4.4\\nmillion short tons. The emission estimates show the industrial\\nSO, emissions increasing steadily with the 20-year rate at\\napproximately 8 percent. Fuel combustion sources continue\\nto be the largest contributor to industrial S0 2 emissions. The\\nemission estimates show the fuel combustion emissions\\ndeclining through the years, primarily from the result of energy\\nefficiency factors. The largest increase in S0 2 can be seen in\\nchemical and allied manufacturing, which is projected to rise\\n30 percent in the 20-year period. Total industrial source S0 2\\nemissions are currently projected to be approximately 4.7\\nmillion tons in 2020. Refer to Figure 4-3 for a graphical\\npresentation of each category\u00e2\u0080\u0099s 2020 contribution.\\n4.4.1 Will the Cap Be Exceeded?\\nSection 406(b) of the CAAA of 1990 states:\\nWhenever the inventory required by this section indicates\\nthat sulfur dioxide emissions from industrial sources,\\nincluding units subject to section 405(g)(6) of the [CAA\\nmay reasonably be expected to reach levels greater than\\n5.60 million tons per year, the Administrator of the [EPA\\nshall take such actions under the [CAA] as may be\\nappropriate to ensure that such emissions do not exceed\\n5.60 million tons per year. Such actions may include the\\npromulgation of new and revised standards of\\nperformance for new sources, including units subject to\\nsection 405(g)(6) of the [CAA], under section 111(b) of\\nthe [CAA], as well as promulgation of standards of\\nperformance for existing sources, including units subject\\nto section 405(g)(5) of the CAA under authority of this\\nsection.\\n(As noted above, the reference to section 405(g)(5) should be\\nto section 405(g)(6).)\\nThe current emission estimates indicate that emissions of\\nSO, from industrial sources will not exceed the 5.6 million\\ntons per year cap through the year 2020. As stated earlier,\\nmore refinement of these estimates is ongoing and a revised\\nprojection will be released with the publication of the next\\nTrends report.\\n4.5 WHAT ARE THE BENEFITS FROM\\nDESULFURIZATION OF DIESEL\\nFUELS?\\nSection 406(a) of the CAAA of 1990 also requires that\\nEPA provide to Congress a report that contains estimates of\\nthe actual emission reduction in each year resulting from\\npromulgation of the diesel fuel desulfurization regulations\\nunder section 214. As a result of the regulation, industry\\nreduced the sulfur content of diesel fuel 0.25 to 0.05 percent\\nas of October 1, 1993. Figure 4.4 displays the emissions for\\non-road sources with and without desulfurization. As shown,\\nemission reductions in the year 1993 are smaller than the other\\nyears since industry lowered the sulfur content of the fuel in\\nOctober of that year. For the years 1994 through 1998, Figure\\n4.4 shows a 51 percent decrease in total vehicle emissions and\\na 400 percent decrease in diesel vehicle emissions, relative to\\nSection 406 of the CAAA: Industrial SO, Emissions 4-3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0091.jp2"}, "92": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nwhat emissions would be without the fuel desulfurization\\nprogram.\\n4.5.1 Why Are Current 1993 Emissions\\nWithout Desulfurization Higher Than\\nthe Values Presented in the 1995 Report\\nto Congress?\\nFor all estimates prior to October 1, 1993, the previous\\ncalculation assumed a sulfur content of 0.20 instead of 0.25\\npercent, since the 0.20 value was the default value listed in\\nEPA\u00e2\u0080\u0099s AP-42 Emission Factor document. 5 When PART5 was\\nreleased, the default value was changed to 0.25. However,\\npast October 1, 1993, the default value was changed to 0.05,\\nsince 0.05 is the regulatory value:\\nSulfur Content Year reflected in data\\nThe 1993 emissions for on-road vehicles without\\ndesulfurization differs from similar values presented in the\\n\u00e2\u0080\u009cNational Annual Industrial Sulfur Dioxide Emission Trends,\\n1995-2015: Report to Congress.\u00e2\u0080\u009d EPA generated the values\\nin the previous report prior to the release of its PART5\\nemissions model, which EPA currently uses to generate S0 2\\nemissions from on-road sources.\\n0.20 (1995 Report) Pre October 1, 1993\\n0.25 (This Report) Pre October 1, 1993\\n0.05 (This Report) All years after October 1, 1993\\n4.6 REFERENCES\\n1. \u00e2\u0080\u009cThe 1985 NAPAP Emissions Inventory (Version 2): Development of the Annual Data and Modelers\u00e2\u0080\u0099 Tapes.\u00e2\u0080\u009d EPA-\\n600/7-89-012a, Air and Energy Engineering Research Laboratory, U.S. Environmental Protection Agency, Research\\nTriangle Park, NC 27711.\\n2. \u00e2\u0080\u009cNational Annual Industrial Sulfur Dioxide Emission Trends, 1995-2015: Report to Congress.\u00e2\u0080\u009d EPA-454/R-95-001.\\nOffice of Air and Radiation. U.S. Environmental Protection Agency, Research Triangle Park, NC. June 1995.\\n3. \u00e2\u0080\u009cNational Air Pollutant Emission Trends Procedures Document, 1900-1996.\u00e2\u0080\u009d EPA-454/R-98-008. Office of Air Quality\\nPlanning and Standards, U.S. Environmental Protection Agency, Research Triangle Park, NC. May 1998.\\n4. \u00e2\u0080\u009cProcedures for Developing Base Year and Future Year Mass and Modeling Inventories for the Tier 2 Final\\nRulemaking,\u00e2\u0080\u009d EPA-420-R-99-034, September, 1999 (found on the web at: http://www.epa.gOv/otaq/tr2home.htm#tsd).\\n5. \u00e2\u0080\u009cCompilation of Air Pollutant Emission Factors, Volume I: Stationary Point and Area Sources,\u00e2\u0080\u009d 4th Edition,\\nSupplement D through 5th Edition, Supplement B, AP-42. U.S. Environmental Protection Agency, Research Triangle\\nPark, NC. 1997.\\n4-4 4.0 Section 406 of the CAAA: Industrial S0 2 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0092.jp2"}, "93": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 4-1. Industrial S0 2 Tier Source Categories\\nDescription Description\\nTierl Tier2 Tier3 Tierl Tier2 Tier3\\nFUEL COMB. INDUSTRIAL\\nCoal\\nbituminous\\nsubbituminous\\nanthracite and lignite\\nother\\nOil\\nresidual\\ndistillate\\nother\\nGas\\nOther\\nInternal Combustion\\nCHEMICAL ALLIED PRODUCT MFG\\nOrganic Chemical Mfg\\nInorganic Chemical Mfg\\nsulfur compounds\\nother\\nPolymer Resin Mfg\\nAgricultural Chemical Mfg\\nPaint, Varnish, Lacquer, Enamel Mfg\\nPharmaceutical Mfg\\nOther Chemical Mfg\\nMETALS PROCESSING\\nNon-Ferrous Metals Processing\\ncopper\\nlead\\naluminum\\nother\\nFerrous Metals Processing\\nMetals Processing NEC\\nPETROLEUM RELATED INDUSTRIES\\nOil Gas Production\\nnatural gas\\nother\\nPetroleum Refineries Related Industries\\nfluid catalytic cracking units\\nother\\nAsphalt Manufacturing\\nOTHER INDUSTRIAL PROCESSES\\nAgriculture, Food, Kindred Products\\nTextiles, Leather, Apparel Products\\nWood, Pulp Paper, Publishing Products\\nRubber Miscellaneous Plastic Products\\nMineral Products\\ncement mfg\\nother\\nMachinery Products\\nElectronic Equipment\\nTransportation Equipment\\nConstruction\\nMiscellaneous Industrial Processes\\nSOLVENT UTILIZATION\\nDegreasing\\nGraphic Arts\\nDry Cleaning\\nSurface Coating\\nOther Industrial\\nNonindustrial\\nSolvent Utilization NEC\\nSTORAGE TRANSPORT\\nBulk Terminals Plants\\nPetroleum Petroleum Product Storage\\nPetroleum Petroleum Product Transport\\nService Stations: Stage I\\nService Stations: Stage II\\nService Stations: Breathing Emptying\\nOrganic Chemical Storage\\nOrganic Chemical Transport\\nInorganic Chemical Storage\\nInorganic Chemical Transport\\nBulk Materials Storage\\nBulk Materials Transport\\nWASTE DISPOSAL RECYCLING\\nIncineration\\nindustrial\\nOpen Burning\\nindustrial\\nIndustrial Waste Water\\nTSDF\\nindustrial\\nLandfills\\nindustrial\\nSection 406 of the CAAA: Industrial S0 2 Emissions 4-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0093.jp2"}, "94": {"fulltext": "Table 4-2. Industrial SO 2 Point and Area Data Source Submittals\\nNational Air Pollutant Emission Trends, 1990-1998\\nID\\noo\\n05\\nco\\n41\\nID\\n00\\n05\\n%n\u00c2\u00b0\\n8\\n\u00c2\u00a3\u00c2\u00a35\\noO c\\no\\nO\\ncp _ to\\n05 LU 05\\nQ.\\nco _\\n05 LU\\n05 n P\\n0\\n-4\u00e2\u0080\u0094\u00c2\u00bb\\nJO\\nCO\\n4\\nto\\n8%\\nLO\\n\u00c2\u00b00 n\\noO\\n8\u00c2\u00a3\\n8\\no\\nCO CO\\n05 LU 0\\nCL^P\\nC$ LJU\\nCL\\n0\\n0\\nCO\\nX X\\nX\\nX X\\nX\\nX\\nX\\nX\\nX\\nXX XX X\\nX X\\nX X\\nX X\\nX\\nX\\nX\\nX X\\nX\\n0\\n0\\nX X\\nQ =5\\n0\\nC 0\\n0\\nE 0 s?\\nP o\\nX X\\n0\\n0 T3 -E iS\\nX X X X X X\\n_ 0 0\\no Q\\n0\\nE\\no\\nSZ\\nm 0 E 0\\nco (O 0 0 S\\nc O Q\\no 0 _P\\n0\\nI\\ni?ssss6\u00e2\u0082\u00acssS l?5^H\\n000000OO o o w\\nZ~Z.-Z.-Z.\\nSZ SI\\n0\\n0\\n0 0 CM\\nsz\\nix x _ 0 -i_ \\\\j vj yj a)*- 0-\u00e2\u0080\u0094\\nzzzz000a.tt:\u00c2\u00abwi-hD $$$5\\nO O (1) 05 +3 0\\n0\\n11\\n.S .E 5\\nc c jr\\nE 05 0 0\\n^00\\nol\\no E\\no o\\n.*2 5\\nXX X\\nX\\nX\\nX\\nX X\\nX\\nX XX\\nX X\\nX X X X X X\\nX X\\n0\\nc\\n0 O -E 0\\n5 c o o L\\n92 0 0\\nc\\nX\\nX X X X X X X\\n0\\n0\\n0\\n3\\nX X\\n0\\n0\\n8 o c t\\nVU\\nI 7=1\\n0\\n0\\n05\\nCM\\n0\\no c\\ny n 0\\n0^2\\n8 3 -S\\n0\\n\u00e2\u0096\u00a0p sz c -g\\nc o 0 S\\nm 0 0 05 ft\\n3 3S 3 S S3\\n0 _Q\\nCl-\\nQ.\\n*0 3\\n0 O\\n0 0\\n0 0\\nCM\\nC\\nE\\nto\\nb\\n0\\n-Q\\n0\\n0\\n0\\na\\nE\\n05\\nc\\n0\\nCO\\n0\\no\\n4\u00e2\u0080\u0094\\nCO\\nLO\\nM\\nLO\\nJO\\nh 5\\nCO\\n0\\nto\\nCO\\na\\n\u00e2\u0096\u00a0c\\n8\\nc\\no\\nlh=\\n\u00e2\u0096\u00a0g 8\\nt\u00c2\u00ab 1\\nas\\nE\\n\u00e2\u0096\u00a08 0\\nc o\\n13\u00c2\u00ae\\nJO T~\\n2\\nI S\\n0\\n-2 J5\\n3\\nCNi CO\\nco\\nuT\\nO\\nz\\n4-6 4.0 Section 406 of the CAAA: Industrial SO, Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0094.jp2"}, "95": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 4-3. Industrial S0 2 Projected Emissions by Selected Source Categories\\n(thousand short tons)\\nSource Category\\n1996\\n1999\\n2002\\n2005\\n2007\\n2008\\n2011\\n2014\\n2017\\n2020\\nFUEL COMB. INDUSTRIAL\\n3,022\\n3,023\\n3,024\\n3,024\\n3,025\\n3,022\\n3,012\\n3,002\\n2,993\\n2,983\\nCoal\\n1,465\\n1,476\\n1,487\\n1,498\\n1,506\\n1,504\\n1,499\\n1,494\\n1,489\\n1,484\\nOil\\n844\\n832\\n819\\n807\\n799\\n796\\n788\\n780\\n771\\n763\\nGas\\n556\\n555\\n555\\n554\\n554\\n555\\n558\\n562\\n565\\n568\\nOther\\n140\\n142\\n145\\n147\\n149\\n149\\n149\\n149\\n149\\n149\\nInternal Combustion\\n17\\n17\\n17\\n18\\n18\\n18\\n18\\n18\\n18\\n18\\nCHEMICAL ALLIED PRODUCT MFG\\n291\\n301\\n312\\n322\\n329\\n333\\n344\\n356\\n368\\n379\\nOrganic Chemical Mfg\\n4\\n4\\n5\\n5\\n5\\n5\\n5\\n6\\n6\\n6\\nInorganic Chemical Mfg\\n204\\n212\\n220\\n227\\n233\\n236\\n245\\n254\\n263\\n272\\nPolymer Resin Mfg\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\nAgricultural Chemical Mfg\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\nPaint, Varnish, Lacquer, Enamel Mfg\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nPharmaceutical Mfg\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nOther Chemical Mfg\\n81\\n83\\n85\\n87\\n89\\n90\\n92\\n94\\n97\\n99\\nMETALS PROCESSING\\n428\\n438\\n447\\n457\\n463\\n467\\n478\\n490\\n501\\n513\\nNon-Ferrous Metals Processing\\n283\\n295\\n306\\n318\\n325\\n329\\n340\\n351\\n362\\n374\\nFerrous Metals Processing\\n128\\n125\\n122\\n120\\n118\\n118\\n117\\n117\\n116\\n116\\nMetals Processing NEC\\n17\\n18\\n19\\n19\\n20\\n20\\n21\\n22\\n23\\n23\\nPETROLEUM RELATED INDUSTRIES\\n337\\n340\\n343\\n346\\n348\\n351\\n358\\n365\\n372\\n380\\nOil Gas Production\\n95\\n91\\n87\\n84\\n81\\n80\\n78\\n76\\n73\\n71\\nPetroleum Refineries Related Industries\\n234\\n241\\n247\\n254\\n258\\n261\\n270\\n279\\n289\\n298\\nAsphalt Manufacturing\\n8\\n8\\n9\\n9\\n9\\n9\\n10\\n10\\n11\\n11\\nOTHER INDUSTRIAL PROCESSES\\n349\\n354\\n359\\n364\\n368\\n370\\n376\\n383\\n389\\n395\\nAgriculture, Food, Kindred Products\\n4\\n4\\n4\\n5\\n5\\n5\\n5\\n5\\n5\\n5\\nTextiles, Leather, Apparel Products\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nWood, Pulp Paper, Publishing Products\\n102\\n104\\n107\\n109\\n111\\n111\\n113\\n115\\n118\\n120\\nRubber Miscellaneous Plastic Products\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nMineral Products\\n230\\n232\\n234\\n235\\n236\\n238\\n241\\n244\\n248\\n251\\nMachinery Products\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nElectronic Equipment\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nTransportation Equipment\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nMiscellaneous Industrial Processes\\n13\\n14\\n15\\n16\\n16\\n16\\n17\\n18\\n19\\n19\\nSOLVENT UTILIZATION\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\n1\\nSTORAGE TRANSPORT\\n3\\n3\\n3\\n3\\n3\\n3\\n4\\n4\\n4\\n4\\nWASTE DISPOSAL RECYCLING\\n6\\n6\\n7\\n7\\n7\\n7\\n8\\n8\\n9\\n9\\nIncineration\\n6\\n6\\n7\\n7\\n7\\n7\\n8\\n8\\n9\\n9\\nOpen Burning\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nIndustrial Waste Water\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nTSDF\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nLandfills\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nAll Industrial SO? Emissions _ 4,437 4,466 4,496 4,526 4,545 4,554 4,582 4,609 4,638 4,665\\nSection 406 of the CAAA: Industrial S0 2 Emissions 4-7", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0095.jp2"}, "96": {"fulltext": "Figure 4-1. S0 2 Emissions by Major Industrial Source Category, 1996\\nNational Air Pollutant Emission Trends, 1990-1998\\n(V\\no\\no\\no\\nD\\no\\nc n\\nCQ\\nO\\no\\n4-8 4.0 Section 406 of the CAAA: Industrial S0 2 Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0096.jp2"}, "97": {"fulltext": "Figure 4-2. Industrial S0 2 Emissions\\n(1900 to 2020)\\nNational Air Pollutant Emission Trends, 1990-1998\\nQ.\\nO\\no\\nCNJ\\nDC\\nLU\\n(suoj *Joqs uonijiu) suojssjujg\\nCO CO\\nuj S\\nh- w\\nCO\\nZ\\nQ S\\n-7 o\\nc\\no\\nQE\\nOh\u00c2\u00ae\\ncojfe\\nOoflO\\nDC 1\\nD-UJ Z\\n^oQ\\nLU LULU\\n^Q_CO\\nl\\no\\nI\u00e2\u0080\u0094\\no\\nQ\\ndO,\\naro.^\\nS\\no\\nLU\\n3X=j\\nLL Q\\nco\\nc\\no\\nCO\\nCO\\nE\\nCD\\n0\\nco\\nD\\nC\\n0\\nCO\\n0\\nCD\\nL_\\no\\nc\\n0\\nCD\\ni\\nCD\\nCO\\nCD\\n\u00e2\u0080\u00a2o\\n0)\\n0\\ni_\\nQ.\\nt_\\n0\\nC\\n0\\nJD\\nO\\nc\\no\\n-C\\nCO\\n\u00e2\u0096\u00a0O\\nc\\n0\\nCO\\ncn\\no\\no\\nTD\\no\\n.c\\n0\\nE\\n0\\no\\n0\\nO\\nCO\\nCO\\nc\\no\\nco\\nCO\\nE\\n0\\no\\nCD\\n05\\n0\\ncl\\nCO\\nc\\n0\\n1\u00e2\u0080\u0094\\n0\\nQ.\\nQ-\\n0\\nO\\n4.0 Section 406 of the CAAA: Industrial SO Emissions 4-9", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0097.jp2"}, "98": {"fulltext": "Figure 4-3. S0 2 Emissions by Major Industrial Source Category, 2020\\nNational Air Pollutant Emission Trends, 1990-1998\\n(U\\no\\no\\no\\no\\n-I\\n4-10 4.0 Section 406 of the CAAA: Industrial SO, Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0098.jp2"}, "99": {"fulltext": "Figure 4-4. S0 2 On-Road Emissions With and Without Desulfurization,\\n1993-1998\\nNational Air Pollutant Emission Trends, 1990-1998\\n(suoj puesnoip) suoissjuig\\nCO\\ncd\\nCD\\nCD\\nCD\\nCD\\nCD\\nCD\\nLO\\nCD\\nCD\\nCD\\nCD\\nCO\\nCD\\nCD\\no\\n4.0 Section 406 of the CAAA: Industrial S0 2 Emissions 4-11\\nAll Vehicles without Desulfurization All Vehicles with Desulfurization\\nDiesel Vehicles without Desulfurization -o Diesel Vehicles with Desulfurization", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0099.jp2"}, "100": {"fulltext": "", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0100.jp2"}, "101": {"fulltext": "Chapter 5.0 National Criteria Pollutant\\nEstimation Methodologies\\n5.1 WHAT INFORMATION IS PRESENTED\\nIN THIS CHAPTER?\\nThis chapter provides a list of the source categories in the\\nNational Emission Trends (NET) data base whose emission\\nestimation methods have changed since the December 1997\\nTrends report and the years that were affected by the\\nmethodology changes. It also provides a brief description of\\nthe revised methods used to estimate emissions from these\\nsources.\\n5.2 WHERE DO I GET INFORMATION ON\\nTHE METHODS USED TO ESTIMATE\\nEMISSIONS FOR SOURCES WHOSE\\nMETHODS DID NOT CHANGE?\\nTo obtain information on how emissions were estimated\\nfor sources not listed in this chapter, you should look in the\\nTrends Procedures Document. 1 The Trends Procedures\\nDocument can be obtained on the Internet using the following\\nwebsite address:\\nhttp://\\\\vw\\\\v.epa.gov/ttn/chief/ei_data.html#ETDP\\nIn addition to the Trends Procedures Document, you\\nshould also look at the chapter entitled \u00e2\u0080\u009cMethodologies That\\nAre New\u00e2\u0080\u009d and Appendix B of the Trends update document. 2\\nMethods used to estimate emissions for several source\\ncategories were changed last year, and descriptions of the\\nchanges are found in the \u00e2\u0080\u009cMethodologies That Are New\u00e2\u0080\u009d\\nchapter of that report. The Trends update document can be\\nfound on the Internet using the following website address:\\nhttp://wvvw.epa.gov/ttn/chief/trends98/emtrnd.html\\nTable 5-1 provides an overview of all sources whose\\nemission estimation methodologies have changed since\\npublication of the Trends Procedures Document.\\n5.3 WHAT OTHER THINGS SHOULD I\\nKNOW ABOUT THE TRENDS\\nESTIMATION METHODS?\\nEach year, the United States (U.S.) Environmental\\nProtection Agency (EPA) compiles emission estimates used in\\nassessing trends in the amounts of criteria pollutants\\ndischarged into the air. Prior to 1993, the main purpose of the\\npublished trends was to portray relative progress in the control\\nof air pollutant emissions nationally. Those estimates were\\nbased on standardized emission inventory procedures using\\naggregate national economic and demographic data. As\\ninterest in, and the need for emission figures for individual\\nStates and metropolitan areas increased, it was obvious those\\ntechniques lacked the precision needed to provide the detailed\\ndata, representative of diverse economic and geographic areas,\\nthat could realistically assess emission reduction efforts at\\nthese smaller scales.\\nIn recent years, the preparation and presentation of\\nnational emission estimates has evolved toward meeting the\\nneed for more detailed and more accurate inventories. To\\nachieve this goal, revised methodologies have been developed\\nthat support the incorporation of detailed State Implementation\\nPlan (SIP) inventories and/or other regional inventories where\\navailable (e.g., Ozone Transport Assessment Group [OTAG],\\nGrand Canyon Visibility Transport Commission [GCVTC],\\nperiodic emission inventories [PEI]). In addition to presenting\\nnational progress in reducing air emissions, local trends in\\nemissions are now presented when possible.\\nBecause of these changes in methodologies,\\ncomparison of values with previous Trends reports is\\nnot a valid exercise You should use caution when\\ncomparing estimates for the years 1985 to 1997 from\\nthis report with values in any previous report.\\nTable 5-2 provides a general overview of where emission\\nvalues were obtained for each State, for both point and area\\nsources. Mobile source emissions are estimated by EPA for\\nall States using the MOBILE model. EPA also prepares utility\\nemission estimates. Table 5-3 indicates the source of data for\\nthe two most important pollutants emitted by utilities (nitrogen\\noxides [NOJ and sulfur dioxide [S0 2\\n5.0 National Criteria Pollutant Estimation Methodologies 5-1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0101.jp2"}, "102": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n5.4 WHAT SOURCE CATEGORIES ARE\\nESTIMATED USING METHODS THAT\\nDIFFER FROM THE PREVIOUS\\nREPORT?\\nTable 5-1 provides a synopsis of the sources whose\\nmethods have changed since the publication of the last Trends\\nreport. 1 Some of the sources listed in Table 5-1 were updated\\nduring the preparation of emissions for the Trends update 2 and\\nwere described in the \u00e2\u0080\u009cMethodologies That Are New\u00e2\u0080\u009d chapter\\nand Appendix B of that report. The shaded rows in Table 5-1\\nindicate source categories that were modified this year and are\\ndescribed in the sections of this chapter that follow.\\n5.5 HOW WERE EMISSIONS FROM NON\u00c2\u00ac\\nROAD SOURCES ESTIMATED?\\nOne of the major changes in the methods used to estimate\\nemissions this year was for non-road sources. EPA\u00e2\u0080\u0099s Office\\nof Transportation and Air Quality (OTAQ, formerly the Office\\nof Mobile Sources [OMS]) has been working on a model that\\nestimates the emissions from these sources for several years.\\nThe April 1999 draft version of the NONROAD model was\\navailable for use this year in estimating emissions from this\\nsource category (http://www.epa.gov/otaq/nonrdmdl.htm).\\nIn large part, emission estimates for volatile organic\\ncompounds (VOC), N0 X carbon monoxide (CO), S0 2\\nparticulate matter (PM) less than 10 microns (PM 10 and PM\\nless than 2.5 microns (PM 25 were calculated using the draft\\nversion of the NONROAD model, for all gasoline, diesel,\\ncompressed natural gas (CNG), and liquefied petroleum gas\\n(LPG) nonroad equipment types at the 10-digit Source\\nClassification Code (SCC) level. There were a few categories\\nthat were not calculated using the NONROAD model. The\\nmethods used to calculate emissions for those non-road\\nsources are described in section 5.5.4 and 5.5.5. In addition,\\nthe NONROAD model does not contain emission factors to\\ncalculate ammonia (NH 3 emissions. As a result, NH 3\\nemissions were calculated outside the model using fuel\\nconsumption estimates that were generated from the\\nNONROAD model. The methods used to calculate other\\npollutants that are not included in the NONROAD model are\\ndescribed in section 5.5.6.\\n5.5.1 What Types of Sources are Included in\\nthe NONROAD Model?\\nThe NONROAD model includes the following general\\ncategories:\\nagricultural;\\nairport support;\\nlight commercial;\\nconstruction and mining;\\nindustrial;\\nlawn and garden;\\nlogging;\\npleasure craft;\\nrailroad; and\\nrecreational equipment.\\nThe model generates emissions at subcategory levels lower\\nthan the general categories listed above. The subcategories are\\nequivalent to 10-digit SCC levels.\\n5.5.2 What Years Were Estimated?\\nCounty-level criteria pollutant estimates for non-road\\nsources were prepared for all years from 1985-1998 inclusive.\\nNational emission estimates were calculated for 1970, 1975,\\nand 1980.\\n5.5.3 Were There Differences in the Methods\\nUsed to Calculate Non-road Emissions\\nfor Different Years?\\nYes. EPA calculated county-level emissions differently\\nfor the periods 1985-1995, 1996, and 1997-1998. The\\nmethods used to calculate county-level emissions for 1985-\\n1995 and 1997-1998 were identical. Two different methods\\nwere used due to time and budget constraints.\\nEPA calculated criteria pollutant emission estimates for\\n1996 using the draft NONROAD model adapted to run on a\\nDEC Alpha UNIX workstation. A set of 385 input files was\\nprepared in order to produce an annual county-level non-road\\nemissions inventory for 1996. These input files included a\\ndefault input file for each State that accounted for average\\nstatewide temperatures and seasonal (summer, fall, winter, and\\nspring) Reid vapor pressures (RVP). Emissions for all\\ncounties in the United States were calculated using the default\\nState input files. In some cases however, the estimates for\\nparticular counties were replaced with county-specific\\nestimates, if those counties had significant differences in their\\nRVP, fuel characteristics due to reformulated gasoline (RFG)\\nand oxygenated fuel requirements, and Stage II controls.\\nFor areas subject to Phase 1 of the Federal RFG program,\\nseparate RVP values were modeled in the 1996 NONROAD\\ninputs for May through September. Oxygenated fuel was\\nmodeled in the areas participating in this program in 1996.\\nFour seasonal emissions files for each run were then added\\ntogether, and the records for each State were combined to\\nproduce a database of annual and daily emissions.\\nOzone season daily emissions were also estimated.\\nWeekday or weekend day emissions must be specified\\nseparately when running the NONROAD model (i.e., annual\\nand daily emissions cannot be generated during the same\\nruns). Because of the time involved in preparing county-level\\nestimates for the whole nation, daily emissions were estimated\\n5-2 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0102.jp2"}, "103": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nby using the summer season emissions generated by the\\nNONROAD model, divided by 92 days rather than performing\\nan additional set of calculations for weekday or weekend day\\nemissions.\\nEmissions for 1985-1995 and 1997-1998 were calculated\\ndifferently than 1996 emissions. The NONROAD model was\\nrun at the national level for all relevant inventory years. Each\\nnational run included three seasonal (i.e., summer, winter, fall/\\nspring combined) NONROAD model runs per year to estimate\\nannual criteria pollutant emissions. Seasonal runs were\\nperformed to account for differences in average seasonal\\ntemperature, as well as RVR Fall and spring were combined\\nsince the average seasonal temperature for those seasons is\\ngenerally equivalent.\\nUsing the results of the national-level runs, we calculated\\na ratio by dividing national 10-digit SCC-level emission\\nestimates for each year by their equivalent 1996 national\\nvalues. County-level emissions were estimated for each year\\nby multiplying each ratio times the 1996 county-level, SCC-\\nlevel emissions. This approach ensures that the sum of all\\ncounty-level emissions for any year are equivalent to the\\nnational-level estimates, but are distributed to the counties\\naccording to the 1996 distribution. This approach was utilized\\ndue to time and resource constraints.\\nBecause the NONROAD model estimates growth in local\\nequipment populations using one national average growth rate,\\nthe effects of growth should be reflected in the national-level\\nruns for each alternate year aside from the base year 1996.\\nThe effects of federal non-road emission standards in future\\nyears (e.g., years beyond 1996) would also be accounted for.\\nBecause the model uses one average growth rate for the whole\\nnation, the approach of using the 1996 county-level inventory\\nas a basis for geographically allocating national inventories for\\nother years was assumed to be reasonable. However,\\ntemperature and fuel inputs to reflect local conditions cannot\\nbe accounted for when doing a national-level run for a\\nspecified year.\\nAs a quality assurance step, category-level emissions\\ngenerated from the 1996 county-level NONROAD model\\nUNIX runs and summed to the national level were compared\\nwith emissions resulting from 3 national, seasonal runs\\n(summer, winter, fall/spring combined). Fall and spring\\nseasonal runs were combined to save resources, since the\\ntemperatures for these two seasons are generally similar. This\\nwas also done to test the viability of the proposed approach for\\nother years, which rely on national-level runs geographically\\nallocated to the county-level using the 1996 county\\ndistribution. If a large disparity existed in the results obtained\\nwhen running the model at the county-level versus the national\\nlevel, it could also potentially result in a discontinuity in the\\nemissions data from 1996 to 1997, or from 1995 to 1996. The\\nresults of these two separate runs are, in fact, reasonably\\ncomparable.\\nRevised emission estimates were also calculated for 1970,\\n1975, and 1980. Only national estimates are available for\\nthese years. We determined source category-specific ratios of\\nthe updated 1985 estimates to the previous Trends values. We\\nthen multiplied that ratio times the previous national Trends\\nnon-road value for each year to develop revised estimates.\\n5.5.4 Were There Non-road Emission Sources\\nThat Were Not Estimated Using the\\nNONROAD Model?\\nYes. Emissions for recreational gasoline powered\\nequipment, aircraft, commercial marine vessels, and\\nlocomotives were estimated using other methods. EPA has\\ndetermined that the draft version of the NONROAD model\\nover estimates the equipment population for recreational\\ngasoline powered equipment, so emissions for that category\\nwere estimated using the Trends methods used before\\nintroduction of the NONROAD model. For the other non\u00c2\u00ac\\nroad emission sources, the NONROAD model does not\\ncurrently include estimation methods for these categories, so\\nthe current Trends method found in the Trends Procedures\\nDocument was used to develop the emission estimates. 1\\n5.5.5 How Were Emissions Estimated for\\nCategories Discussed in Section 5.5.4\\nAbove?\\nAs indicated above, the NONROAD model is still in draft\\nform, and emission estimates for certain categories are still\\nundergoing review. For example, large populations are\\nreported for recreational gasoline equipment. This results in\\nemission estimates that are significantly higher than prior year\\nestimates. For this reason, EPA requested that emission\\nestimates from the existing Trends data base be used in place\\nof the NONROAD model estimates for this category.\\nCommercial aircraft and general aviation estimates for\\n1997 and 1998 were developed from 1996 values using\\nupdated landing-takeoff operations data from the Federal\\nAviation Administration (FAA) as growth factors. Military\\naircraft, unpaved airstrips, and aircraft refueling emissions\\nwere grown from 1996 using growth factors consistent with\\nthe current draft version of the Economic Growth Analysis\\nSystem (EGAS). 3 Information on how the 1996 emission\\nestimates for these sources were developed can be found in the\\nTrends Procedures Document. 1\\nEPA\u00e2\u0080\u0099s OTAQ prepared 1995-1998 VOC, NO x CO, and\\ntotal PM national emission estimates for commercial marine\\ndiesel engines. PM 10 was assumed to be equivalent to PM, and\\nPM 2 5 was estimated by multiplying PM I0 emissions by a factor\\nof 0.92. These new national estimates were distributed to\\ncounties using the geographic distribution in the existing 1996\\nNET data base [i.e., the National Acid Precipitation\\nAssessment Program (NAPAP) distribution, or the State-\\nsupplied distribution, if a State had submitted data under\\nOTAG for these categories]. Commercial marine emissions\\n5.0 National Criteria Pollutant Estimation Methodologies 5-3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0103.jp2"}, "104": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nwere not reported under the same SCC for all States in the data\\nbase. For example, some States reported commercial marine\\ndiesel emissions under the SCC 2280000000, which could\\npotentially include other fuel types (e.g., residual, gasoline).\\nTherefore, a distribution was established based on emissions\\nfor all commercial marine SCCs. Because the OTAQ\\nestimates included emissions from residual-fueled vessels,\\nemissions corresponding to this SCC were removed, as well as\\nemissions from the general SCC 2280000000. Sulfur dioxide\\nemissions reported for residual-fueled vessels were not\\nremoved, however, since OTAQ did not supply revised\\nemissions for this pollutant.\\nIn addition, records for several States had emissions for\\nsome pollutants, including S0 2 and PM 10 but no VOC, NO x\\nor CO emissions. We estimated the emissions for these\\npollutants, by using a national average ratio of VOC/PM 10\\nNO X /PM 10 and CO/PM 10 which were calculated from the\\navailable inventory data. These ratios were then applied to the\\nPM, 0 emissions to estimate the missing VOC, NO x and CO\\nemissions.\\nFor the years 1985-1994, we calculated the ratio of the\\n1995 revised OTAQ commercial marine emissions to the\\nprevious 1995 Trends emissions values for each pollutant.\\nThis ratio was then applied to emission estimates for the\\nfollowing SCCs: commercial marine diesel (2280002),\\ncommercial marine residual (2280003), and commercial\\nmarine unspecified fuel (2280000). This method was used to\\navoid a large disparity between existing Trends estimates and\\nrevised OTAQ estimates (which were only available back to\\n1995). We did not perform any additional data augmentation\\nfor these years.\\n1997 and 1998 emission estimates for commercial\\ngasoline, commercial coal, and military marine vessels were\\ngrown from 1996 using growth factor values that were\\nconsistent with the current draft version of EGAS.\\n5.5.6 Were Any Pollutant Estimates Prepared\\nDifferently for Non-road Sources?\\nYes, lead (Pb) and NH V Pb was estimated using methods\\ndescribed in section 5.18 of the Trends Procedures Document. 1\\nFor NONROAD model categories, NH 3 emissions were\\ncalculated for the years 1990-1998, based on county-level fuel\\nconsumption estimates obtained from NONROAD model runs.\\nFuel consumption estimates were not available for LPG and\\nCNG-fueled equipment. Emission factors provided by EPA\u00e2\u0080\u0099s\\nOTAQ were then applied to these activity data to estimate NH 3\\nemissions for gasoline equipment (without catalysts) and\\ndiesel-fueled equipment. The emission factors were derived\\nprimarily from light-duty on-road vehicle emission\\nmeasurements, and extrapolated to nonroad engines on a fuel\\nconsumption basis.\\nAs indicated above, emission estimates for recreational\\ngasoline equipment were maintained from the previous version\\nof the NET. However, recreational gasoline NH 3 emissions\\nwere calculated differently. Recreational gasoline equipment\\nNH 3 emissions were calculated based on the NONROAD\\nmodel fuel consumption estimates. These estimates were then\\nredistributed to existing NET records. This was done to avoid\\nhaving records in the inventory that only contained NH 3\\nestimates, since many of the SCCs reported in the NONROAD\\nmodel for this category were not present in the existing Trends\\ninventory. In addition, many States had previously reported\\nthese emissions under the general SCCs 2260001000 (all 2-\\nstroke gasoline recreational vehicles) and 2265001000 (all 4-\\nstroke gasoline recreational vehicles), instead of the more\\nspecific recreational equipment types.\\nFor aircraft, commercial marine, and locomotive\\ncategories, national fuel consumption estimates for 1996 were\\nobtained from various sources. Jet fuel and aviation gasoline\\nconsumption for general aviation and commercial aircraft were\\nobtained from the \u00e2\u0080\u009cFAA Aviation Forecasts Fiscal Years,\\n1998-2009.\u00e2\u0080\u009d 4 For aircraft categories, NH 3 emission factors\\ndeveloped for diesel engines were applied to all fuel\\nconsumption estimates, since aviation gasoline consumption\\nwas determined to be relatively small compared to jet fuel, and\\nthe aircraft SCCs are not defined by fuel type. Diesel\\nconsumption estimates for locomotives were obtained from\\n\u00e2\u0080\u009cLocomotive Emission Standards Regulatory Support\\nDocument (RSD).\u00e2\u0080\u009d 5 For commercial marine, data for distillate\\nand residual fuel oil were reported in \u00e2\u0080\u009cFuel Oil and Kerosene\\nSales.\u00e2\u0080\u009d 6\\nTo develop NH 3 emissions for 1997 and 1998, 1996 base\\nyear NH 3 emissions for these categories were projected for\\nthese categories using growth factors. S0 2 emissions were not\\nsupplied by OTAQ for commercial marine and locomotives,\\nand estimates for this pollutant were projected using growth\\nfactors as well. NH 3 emissions were reported in the NET\\ndatabase for commercial marine and locomotive categories for\\nhistoric years (i.e., 1990-1995); no changes were made to\\nthese historic estimates. Historic NH 3 emissions were not\\navailable for aircraft, so there is a disparity between 1995 and\\n1996 for NH 3 emissions for this category.\\nOnce annual NH 3 emissions were calculated, summer\\nseason daily emissions were estimated using seasonal profiles\\navailable from the 1985 NAPAP study. SCC-specific summer\\nseasonal fractions were applied to the annual emissions to\\ngenerate summer season emissions, which were then divided\\nby 92 days to estimate summer season daily emissions.\\n5-4 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0104.jp2"}, "105": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n5.6 WHAT CHANGES WERE MADE IN THE\\nMETHOD USED TO ESTIMATE\\nNONUTILITY POINT AND AREA\\nSOURCE EMISSIONS?\\nEPA has tried over the last several years to ensure that the\\nNET data base reflects State developed emission estimates\\nwhenever feasible. For example, 1990 NET emission\\nestimates include State-developed data from OTAG and\\nGCVTC inventories. Emissions for years following 1990\\nwere supplemented with data from the Aerometric Information\\nRetrieval System (AIRS). PEI and annual submission of\\nemissions data for major point sources are required under the\\nCAAA. As part of the PEI requirements, States containing\\nnonattainment areas (N AAs) needed to submit a PEI for 1996.\\nConsequently, one of EPA\u00e2\u0080\u0099s goals was to include data\\ndeveloped by the States as part of the 1996 PEI effort in the\\nNET. While the CAAA only requires submittal of ozone\\npollutant data for the PEI requirements, annual point source\\nreporting is designed to cover all pollutants. Additionally, in\\nthe guidance provided to the States on the PEI submittal\\nprocess, EPA encouraged States to submit emission estimates\\nfor all pollutants, since the NET contains estimates for all\\ncriteria pollutants and is to be the ultimate repository of the\\nState data. To reduce the burden of preparing this inventory,\\nEPA gave each State a copy of the 1996 NET inventory as a\\nstarting point in preparing their 1996 PEI.\\nIn the past, EPA has estimated emissions for this group of\\nsources by growing emissions using growth factors derived\\nfrom the U.S. Department of Commerce, Bureau of Economic\\nAnalysis (BEA). As mentioned above, some data derived\\nfrom AIRS was also used to supplement the emissions in\\ncertain years.\\n5.6.1 What Steps Were Required to\\nIncorporate State PEI Data Into the\\nNET?\\nThe incorporation of the 1996 State/Local emission\\ninventory data is a five step process:\\nData Collection;\\nQuality Control (QC);\\nData Augmentation;\\nQuality Assurance (QA); and\\nData Loading.\\nIn the data collection step, EPA solicited PEI and annual\\npoint source data from the States. There were four acceptable\\nformats States could use to submit their data: 1) the NET\\nInput Format, 2) through AIRS/AIRS Facility Subsystem\\n(AFS), 3) the Electronic Data Interchange X.12 format, and\\n4) the NET Overwrite Format.\\nIn the QC step, EPA evaluated the data received to ensure\\nthat States had correctly characterized, on the 1996 Emission\\nInventory Submittal Form, the data they submitted (e.g.,\\ngeographic coverage, pollutants, SCCs, annual and daily\\nemissions), that the data were formatted correctly; that\\nmandatory data elements were included, and the priority SCCs\\nneeded to incorporate the data were present (e.g., nonutility\\npoint and stationary area source SCCs). Any problems found\\nwere followed-up by a phone call to the State/local agency for\\nreview and resolution. If basic problems could not be\\nresolved, the data were not included in this version of the\\nNET. Data not included in this version of the NET will be\\nincorporated in FY 2000.\\nIn the data augmentation step, data elements required for\\nthe regional scale modeling or this report, that were not\\nsupplied in the State data set, were added to the NET. EPA\\nneeds a complete inventory containing VOC, NO x CO, S0 2\\nPM ]0 PM 25 and NH 3 We added emission estimates to the\\nNET for any of these pollutants if they were not included in\\nthe State submitted data. Each data element was characterized\\nas \u00e2\u0080\u009cmandatory submission\u00e2\u0080\u009d or \u00e2\u0080\u009cdata can be augmented.\u00e2\u0080\u009d As\\npart of the QC step, all data received was checked to ensure\\nthat data elements classified as mandatory submission were\\nincluded in the data supplied by the States.\\nIn the QA step, data were checked for reasonableness.\\nQ A reports highlighting questionable data were developed and\\nsent to the States for review. Questionable data were either\\nconfirmed by the State as correct, corrected by the State, or in\\nthe case where the State did not respond, replaced using the\\ndata augmentation methods. The QA reports that were sent to\\nStates for review included:\\nTier 2 Summary;\\nTop 20 Plants for Each Pollutant with Comparison to\\nCurrent Data;\\nNET Plants Not in the State Data;\\nGeographic Coordinate Exceptions;\\nStack Parameter Exceptions; and\\nLarge Sources Without Emission Controls.\\nIn the data loading step, EPA loaded State data that met\\nthe QA criteria, or was resolved during the QA step, into the\\nNET data base. This resulted in a fully revised 1996 point and\\narea source file.\\n5.6.2 How Many States Submitted Data for\\nthe 1996 PEI Effort?\\nPoint source data for 34 States and area source data for 13\\nStates was received as part of the PEI data incorporation\\neffort. Figure 5-1 is a map of the United States that indicates\\nwhich States provided 1) point source data that were utilized,\\n2) point source data that were not utilized at this time due to\\ndata quality problems, 3) point and area source data that were\\nutilized, and 4) no data.\\n5.0 National Criteria Pollutant Estimation Methodologies 5-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0105.jp2"}, "106": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nFor the majority of States, the PEI point source submittals\\nwere made to the AFS. Some States submitted data in\\nalternative formats, primarily using the NET Input Format.\\n5.6.3 Were Any State-Supplied Data Rejected\\nin the QC Phase?\\nYes. A few States\u00e2\u0080\u0099 data were rejected either due to\\nproblems with data completeness, data format, or both. EPA\\nis working to resolve these problems with the individual States\\nand hopes to include data from these States in the next release\\nof the NET. These States are indicated in Figure 5-1 as States\\nwhose data will be processed in 2000.\\n5.6.4 What Types of Data Were Augmented\\nin the Data Augmentation Step?\\nAs mentioned above, the NET contains emission estimates\\nfor all criteria pollutants (except Pb). Thus data elements\\nand/or pollutant emissions that were missing in the State\\nprovided data needed to be augmented. The data augmentation\\nprocedure included augmenting information related to stack\\nparameters (height, diameter, velocity, flow, temperature),\\nlocation information (latitude and longitude), operating\\nschedule (hours per day, days per week, hours per year,\\nseasonal throughput), and emission estimates for pollutants not\\nincluded in the State submittals. A detailed list of the items\\naugmented in the data augmentation phase and the individual\\nsteps taken to augment the various data elements is provided\\nin Barnard et. al. 7 and in the draft Trends Procedures\\nDocument currently being revised. 8\\n5.6.5 What Quality Assurance Steps Were\\nTaken to Ensure That the State Data\\nWere Incorporated Correctly?\\nQuality assurance was an essential element of the data\\nincorporation process. Extensive internal review of the data\\nwas performed to ensure that the data were retrieved and\\nformatted correctly and that the data augmentation process was\\nperformed correctly. On-going reviews were made of the data\\nto ensure that there were not duplicate records, that emissions\\nvalues were not \u00e2\u0080\u009cout of range\u00e2\u0080\u009d, and that the values for stack\\nparameters were within normal operational values.\\nThe most important part of the QA program was State\\nreview of the retrieved and augmented data. EPA prepared a\\nreview package for each State submitting data. The review\\npackage consisted of a number of reports and tables showing\\na variety of information about the preliminary data set.\\nIn the past, QA of the NET inventory focused almost\\nexclusively on the emission estimates. Due to the NET\u00e2\u0080\u0099S\\nchange in focus to a modeling inventory, QA of the NET was\\nexpanded to cover additional data elements including stack\\nparameters, geographic coordinates, emission control data, and\\noperating schedule data.\\nTo QA stack parameters, upper and lower limits were\\ndeveloped for each stack parameter carried in the NET. The\\nStack Exception Report in the QA package listed stacks in the\\nNET where one or more of the parameters was above the\\nupper bound or below the lower bound. High and low values\\nnot corrected by the States were replaced with the\\ncorresponding upper or lower bound value. The acceptable\\nranges for each stack parameter are listed below:\\nHeight\\nDiameter\\nTemperature\\nVelocity\\n0 ft to 1,250 ft\\n0 ft to 50 ft\\n32\u00c2\u00b0F to 2,250\u00c2\u00b0F\\n0 ft/sec to 650 ft/sec\\nTo QA geographic coordinates, maps were generated for\\neach State showing any facilities that were located outside of\\ntheir State borders when plotted using the geographic\\ncoordinates supplied by the State. Coordinates not corrected\\nby the States were replaced with the coordinates for the county\\ncentroid based on the State and county codes provided by the\\nState.\\n5.6.6 What Did EPA Do With Comments\\nReceived by the States?\\nIn the early review of the data, several States indicated\\nthat the emissions for their ozone precursor pollutants were\\nnot correct. The original downloads from AFS were designed\\nto retrieve the default emissions value. However, several\\nStates indicated that they typically stored emissions data in one\\nof the alternative emission fields. As a consequence, EPA\\nsurveyed the States that submitted data to determine which\\nStates submitted emissions data in something other than the\\ndefault emissions field. Data for those States was retrieved a\\nsecond time and augmented as required. The emissions for\\nthose States were re-summarized and sent back to the States\\nfor a final review.\\nOnce comments from all of the review packages were\\nreceived, modifications to the emissions or process data were\\nmade based on the State comments. Modification to the AFS\\nPEI data were made to reflect either new data from the\\nadditional downloads, modifications based on the review\\npackages sent out to the States, or based on data that remained\\nanomalous (e.g., stack flow rates).\\nOne portion of the State review package was a list of\\nplants not included in the PEI submittals that were in the\\nversion of the 1996 NET provided to the States as a starting\\npoint for PEI preparation. Several States provided comments\\non that table indicating that 1) some or all of these facilities\\nshould be maintained, and 2) indicating that while they should\\nbe maintained, the emissions should be modified to reflect\\nmore accurate State-supplied values. The data for these plants\\nwere extracted from the NET and maintained in a separate file.\\n5-6 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0106.jp2"}, "107": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nSince the review packages only provided plant totals, ratios of\\nold to new plant emissions were used to adjust the values of\\neach segment\u00e2\u0080\u0099s emissions and then the data were updated in\\nthe file.\\n5.6.7 Was There Any Additional Data\\nAugmentation?\\nYes. In addition to criteria pollutants, the NET also\\nhouses estimates of NH 3 emissions. None of the States\\nsubmitting PEI data submitted NH 3 emissions. As a\\nconsequence, the NH 3 emissions from the 1996 NET needed\\nto be added back into the revised data base. Two steps were\\ntaken to perform this augmentation. First, plant-level total\\nNO x emissions were calculated for the PEI data submitted by\\nthe States. Then plant-level summaries of NH 3 from the NET\\nwere developed. Where a match could be made using the State\\nFederal Information Processing Standards (FIPS) code, county\\nFIPS code, and plant identification (ID) code, segment-level\\nemissions for NH 3 were calculated using the following\\nequation:\\nNH 3 seg (NO x seg/NO x plant) NH 3 plant\\nwhere:\\nNH 3 seg\\nNO x seg\\nNO x plant\\nNH 3 plant\\nsegment-level NH 3 emissions\\nPEI segment-level NO x emissions\\nPEI plant-level NO x emissions\\nNET plant-level NH 3 emissions\\nIn order to maintain the NH 3 totals currently in the NET,\\nNH 3 -only plant/segment-level records were added for those\\nfacilities that did not match plants in the PEI submitted data.\\n5.6.8 Were There Emissions From Any\\nSources Submitted by the States That\\nWere Not Incorporated into the NET?\\nA few source categories were not updated using State-\\nsupplied PEI data. These source categories were not updated\\nbecause EPA feels that the consistent methodology and the\\nquality of the data involved in the calculation of emissions\\nfrom these categories is at or above that provided by the States.\\nFor point sources, State-supplied utility emissions data for\\nsegments with SCCs beginning with 101 were not retained.\\nFor area sources, the categories not included from State data\\nwere on-road mobile and non-road. This approach will be\\nrevised in 2000, as data issues are resolved between the States\\nand EPA for the utility and mobile categories.\\n5.6.9 How Were Nonutility Point and Area\\nSources for 1997 and 1998 Developed?\\nThe PEI data incorporation effort was only for 1996\\nemissions. Thus, EPA had to develop 1997 and 1998\\nemissions internally. Emissions for nonutility point sources\\nand many area sources were developed using growth factors.\\nTo develop 1997 and 1998 emission estimates, EPA\\ncompiled a set of emission growth factors to apply to the 1996\\nNET inventory. For the most part, these growth factors were\\ndeveloped using procedures that are similar to those used by\\nEGAS. 3 The current, publically available version of EGAS is\\nversion 3.0. Because EGAS version 3.0 was released in 1995,\\nEPA has recently been working to develop an EGAS Version\\n4.0. The growth factors used for developing 1997 and 1998\\nestimates were developed using the draft version of EGAS 4.0.\\nAs part of the EGAS version 4.0 development effort, EPA has\\nobtained more recent data/models and updated some of the\\nunderlying EGAS files. Two of the major changes that EPA\\nhas been performing are: (1) incorporating new economic\\nmodels from Regional Economic Models, Inc. (REMI); and\\n(2) revising the EGAS 3.0 crosswalk that is used to assign\\nREMI model-derived growth factors to SCCs. The REMI\\nmodels, which included 72 modeling regions in EGAS 3.0,\\ncover the continental United States. While many modeling\\nregions cover an entire State, some States have separate\\nmodels for ozone NAAs and rest-of-state areas. For this\\neffort, updated REMI models were available that provide\\nhistorical (through 1996) and forecast (through 2035)\\nsocioeconomic data for each of 75 modeling regions in the\\nUnited States (three new modeling regions were added in\\nNorth Carolina). 9 As part of the revisions to the EGAS 3.0\\ncrosswalk, EPA reviewed each of the previous SCC\\nassignments and incorporated new assignments for over 2,600\\nadditional SCCs.\\nThe EPA applied REMI model-derived growth factors to\\npoint sources at the Standard Industrial Classification (SIC)\\ncode-level whenever SIC code information was available in\\nthe inventory. Because REMI\u00e2\u0080\u0099s models provide output for\\n172 economic sectors, which are roughly equivalent to 3-digit\\nSIC codes, REMI output was first directly matched to the SIC\\ncode information available from the point source component\\nof the NET inventory. For some point source records, SIC\\ncode information was missing, available at less than a 3-digit\\nSIC code level, or invalid (did not represent a valid SIC code).\\nFor these point source records, EPA assigned REMI model-\\nderived growth factors to SCCs using the revised EGAS\\ncrosswalk. Because the REMI models do not include Alaska\\nand Hawaii, it was necessary to utilize a different source of\\nprojections data for these States. The BEA released a set of\\ngross State product (GSP) projections in 1995. 10 These\\nprojections, which are generally available at a 2-digit SIC code\\nlevel, were used to develop growth factors for Alaska and\\nHawaii. The BEA-derived growth factors were first matched\\nwith point sources in the inventory at the 2-digit SIC code\\n5.0 National Criteria Pollutant Estimation Methodologies 5-7", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0107.jp2"}, "108": {"fulltext": "National Air Pollutant Emission Trends 1900 1998\\nlevel. For point sources with missing/invalid SIC code\\ninformation, and for all area sources, EPA matched BEA data\\nwith emission sources using an updated EGAS 3.0 crosswalk\\nmatching BEA sectors with SCCs.\\nEGAS 3.0 includes a number of models that project\\nenergy consumption by sector and fuel type (e.g., residential\\nnatural gas consumption). The revisions to the energy\\nconsumption modules in EGAS 3.0 have not yet been\\ncompleted. Because these updates are expected to include the\\nuse of Department of Energy (DOE) energy projections data,\\nEPA compiled the DOE\u00e2\u0080\u0099s forecast data for use in adjusting the\\nREMI/BEA data for projected changes in energy intensity.\\nSpecifically, the EPA calculated the following national energy\\nintensity factors for 1996, 1997, and 1998:\\nResidential fuel combustion projected delivered\\nenergy by fuel type divided by projected residential\\nfloor space;\\nCommercial/institutional fuel combustion projected\\ndelivered energy by fuel type divided by projected\\ncommercial floor space; and\\nIndustrial fuel combustion projected delivered\\nenergy by fuel type for both specific industries (e.g.,\\nrefining industry) and for total industrial fuel use\\ndivided by projected constant dollar industrial output\\n(specific industry or total industrial output).\\nNext, EPA calculated the ratios of national 1996 energy\\nintensity to both the national 1997 and 1998 energy intensity\\nfor each sector/fuel type. For residential natural gas\\nconsumption, for example, EPA developed 1996:1997 and\\n1996:1998 ratios of residential natural gas consumption per\\nsquare foot of residential floor space. These ratios were then\\nused to adj ust the EGAS modeling region-specific REMI/BEA\\npopulation-based residential fuel consumption growth factors.\\nFinally, for VOC emissions, controls were implemented\\nfor several maximum achievable control technology (M ACT)\\nsources. If a source category was subject to MACT in either\\n1997 or 1998, the 1996 control efficiency for that source was\\ncompared with the control efficiency that the MACT control\\nwould have on VOC. If the 1996 control efficiency was\\ngreater than or equal to the MACT control efficiency then the\\ndata was maintained at the 1996 level. If the 1996 control\\nefficiency was lower than the MACT standard, then\\nuncontrolled emissions were back-calculated using the 1996\\ncontrol efficiency and then controlled emissions were\\ncalculated from the uncontrolled levels using the MACT\\ncontrol efficiency. The MACT control efficiency value was\\nalso inserted into the data base field for control efficiency. It\\nwas assumed that the MACT controls operated for the entire\\nyear, even if they were not scheduled to come on-line until the\\nmiddle to latter part of the year.\\n5.7 WHAT OTHER METHODOLOGY\\nCHANGES WERE THERE?\\nMethodology changes or changes in the underlying data\\nused to calculate emissions were made for agricultural\\nlivestock, structural fire, and prescribed burning emissions. In\\naddition, corrections were made in how on-road mobile NO x\\nemissions were calculated to account for the heavy-duty NO x\\ndefeat device on heavy-duty diesel engines. (See Section\\n5.7.4.)\\n5.7.1 What Changes Were Made in How\\nAgricultural Livestock Emissions Were\\nCalculated?\\nEPA had calculated PM and NH 3 emissions from\\nagricultural livestock sources using U.S. Department of\\nAgriculture (USDA) Census of Agriculture data on animal\\npopulations. The Census of Agriculture is conducted every 5\\nyears. Thus, we had been required to develop a methodology\\nthat could be used to estimate emissions in years between the\\npublication of the Census of Agriculture data. EPA used BEA\\nState-level farm sector growth factors to estimate emissions\\nfor the years between Census of Agriculture publications. For\\nthe time period that EPA had estimated emissions from this\\nsource category (1990-1997) only one Census of Agriculture\\npublication had been prepared (1992). The 1997 Census of\\nAgriculture was released in the spring of 1999. An evaluation\\nof the actual statistics on livestock populations following\\nrelease of the 1997 Census of Agriculture indicated that the\\nlivestock population data for 1997 was very similar to the\\n1992 data. However, the NET inventory had shown\\napproximately a 25 percent drop in total NH 3 emissions from\\n1992 to 1997 which was due almost entirely to an\\napproximately 40 percent drop in emissions in the livestock\\ncategory. Apparently agricultural commodity prices dropped\\nbetween 1992 and 1997, but livestock populations stayed more\\nor less stable. Since the BEA statistics use commodity prices\\nrather than animal population data, the post-1992 inventories\\nwould be underestimated.\\nThus EPA decided that the emission estimates for this\\nsource category should be revised using more appropriate data\\non animal populations. The 1987 Census of Agriculture data\\nwere obtained and in conjunction with the 1992 and 1997 data\\na linear estimation method was developed to predict animal\\npopulations for intermediate years and to project to 1998. The\\nlinear estimates developed were State and animal specific. In\\nsome cases, development of the linear regression used to\\nestimate animal populations resulted in negative values. In\\nthose cases, the animal population was set to zero.\\nUsing the revised animal population data with the current\\nemission factors 1 revised estimates were developed. The\\nchanges only affected NH 3 and PM emission estimates.\\n5-8 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0108.jp2"}, "109": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n5.7.2 What Changes Were Made in How\\nStructural Fire Emissions Were\\nCalculated?\\nEPA has an on-going program to improve the quality of\\nemission estimates. That program, the Emission Inventory\\nImprovement Program (EIIP) routinely evaluates the methods\\nused to estimate emissions from various sources. Recent work\\nby the EIIP had identified a revision to the loading factor used\\nto estimate emissions from structural fires. The revised value\\nfor the loading factor was obtained from the California Air\\nResources Board. 12\\nUsing the revised loading factor, emission estimates were\\nrevised starting with 1990. Since several States submitted data\\nfor this source during the OTAG data collection process,\\nrevised and updated 1990 emission estimates for this source\\nwere developed by EPA only for non-OTAG States. Once the\\n1990 estimates were revised, 1991-1995 estimates were\\ncalculated by usi ng a growth factor developed for the on-going\\nrevision to EGAS. The growth factor for the revised version\\nof EGAS was developed using a regression equation that\\nrelates national population to the amount of material burned in\\nstructural fires. State-level population is then used as an input\\nto predict the amount of material burned in each State, using\\nthe regression equation. Both OTAG and non-OTAG\\nestimates were grown.\\nEstimates for 1996 were developed using updated activity\\ndata and the California Air Resources Board\u00e2\u0080\u0099s loading factor\\nfor non-OTAG states. OTAG States were grown using the\\nEGAS growth factors. Then, as part of the 1996 PEI data\\nincorporation effort, 1996 emissions were replaced by State-\\nsupplied data obtained during the PEI effort.\\nEstimates for 1997 and 1998 were developed identically\\nto how the base 1996 data were developed, except that there\\nwas no replacement with State-supplied data, since there was\\nno equivalent to the PEI data for those years.\\n5.7.3 What Changes Were Made in How\\nPrescribed Burning Emissions Were\\nCalculated?\\nEPA updated prescribed burning emissions estimates to\\nbetter reflect data now available with which to calculate\\ngrowth in this sector. In earlier versions of the NET,\\nemissions for prescribed burning were grown using population\\nas a surrogate. EPA felt that population was not an\\nappropriate growth surrogate for prescribed burning. A\\nmethod developed for the Section 812 Prospective 13 study\\nwhich held private land acreage constant, but develops a\\ngrowth index for public lands based on national statistics for\\nacres burned, was initiated this year. The technique uses 1990\\nestimates as a base year, since values for 1990 include actual\\ndata for a number of States, especially those in the GCVTC\\ninventory.\\nEPA used information on the fraction of public including\\nState-owned and private land from the Section 812\\nProspective study to allocate a portion of the emissions to each\\nof these components. Then, a national ratio of acres burned on\\npublic lands was developed using U.S. Forest Service data. 14\\nGrowth factors were then developed by calculating a ratio for\\nthe year of interest relative to 1990 (the base year). The\\ngrowth factor was then multiplied by the fraction of emissions\\nattributable to public lands. This value was then added back\\nto the remaining emissions (i.e., those attributable to private\\nlands) to obtain the emissions for each year. This is a rough\\nestimate. The actual number of acres burned each year varies\\ngreatly and is a function of fuel moisture, fuel density,\\nmeteorology, and other factors.\\n5.7.4 How Did EPA Account for Emissions\\nfrom Heavy-Duty Diesel Engines that\\nUsed the NO x Defeat Device?\\nOn October 22, 1998, EPA reached a settlement\\nagreement with seven manufacturers of diesel truck engines.\\nEPA had found that the engines in as many as 1.3 million\\ntrucks built over the last 10 years had devices that defeated\\npollution controls. Those allegations were related to excessive\\nNO x emissions during highway driving that were not occurring\\nduring engine certification testing. The engine electronic\\ncontrol module would switch to those fuel-efficient, but high\\nNO x operation modes during highway driving. Federal\\nofficials considered such engine control software \u00e2\u0080\u009cdefeat\\ndevices\u00e2\u0080\u009d, which are illegal under the federal laws.\\nFor purposes of this report, a defeat device is a vehicle\\ncomponent or software which allows excess emissions to be\\nproduced during operating modes which are not explicitly\\ncovered by a certification test while still controlling emissions\\nduring the certification test. In the case of the heavy-duty NO x\\ndefeat device, the device was active (shut off emission control\\nsystems) during steady-state operating modes such as cruising\\ndown the freeway, but was mostly inactive during transient\\noperation. It was built into heavy-duty diesel vehicles\\n(HDDVs) beginning in the 1988 model year, and completely\\nremoved by the 2000 model year. In the late 1980\u00e2\u0080\u0099s and early\\n1990\u00e2\u0080\u0099s the defeat device was being phased into the fleet and\\nwas mostly confined to the heavy end of the heavy-duty\\ndiesels (8a and 8b vehicles). However, by the mid to late\\n1990\u00e2\u0080\u0099s it was widespread on virtually all of the heavy end\\nengines and most of the medium and light end heavy-duty\\ndiesels.\\nEPA\u00e2\u0080\u0099s MOBILE model used to calculate emissions from\\non-road vehicles is designed based on engine certification\\ntesting. Thus, the use of the defeat devices by HDDVs caused\\nthe emission factors calculated by those models to\\nunderestimate emissions from these vehicles. In order to\\ndetermine that actual emissions arising from the use of these\\ndevices, EPA developed a series of spreadsheet models to\\nprovide corrected emission factors for heavy-duty vehicles that\\n5.0 National Criteria Pollutant Estimation Methodologies 5-9", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0109.jp2"}, "110": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nwould account for the underestimated emissions. 15 EPA\u00e2\u0080\u0099s\\nOTAQ spreadsheets contain multiplicative factors representing\\nthe ratio of HDDV NO x emissions with the defeat devices to\\nthe HDDV NO x emissions without the defeat devices. These\\nfactors differ by calendar year, roadway type, and vehicle\\nspeed. The HDDV NO x emissions, calculated using the\\nMOBILE5b HDDV NO x\\nemission factors, were revised by multiplying the appropriate\\nfactor at the State/county/roadway type level of detail for the\\nyears 1990 through 1998. Additional details on the\\nspreadsheet models can be found at the following website\\naddress:\\nhttp://www.epa.gov/OMSWWW/m6.htm\\n5.9 REFERENCES\\n1. \u00e2\u0080\u009cNational Air Pollutant Emission Trends Procedures Document, 1900-1996,\u00e2\u0080\u009d EPA-454/R-98-008. Office of Air Quality\\nPlanning and Standards, U.S. Environmental Protection Agency, Research Triangle Park, NC. May 1998.\\n2. \u00e2\u0080\u009cNational Air Pollutant Emission Trends Update, 1970-1997,\u00e2\u0080\u009d EPA-454/E-98-007, U.S. Environmental Protection\\nAgency, Research Triangle Park, NC. December 1998.\\n3. \u00e2\u0080\u009cEconomic Growth Analysis System: Version 3.0,\u00e2\u0080\u009d software, reference manual, and user\u00e2\u0080\u0099s guide, U.S. Environmental\\nProtection Agency. Available for download from http://www.epa.gOv/ttn/chief/ei_data.html#EGAS. August 1995\\n4. \u00e2\u0080\u009cFAA Aviation Forecasts Fiscal Years, 1998-2009,\u00e2\u0080\u009d Office of Aviation Policy and Plans, Federal Aviation\\nAdministration. March 1998.\\n5. \u00e2\u0080\u009cLocomotive Emission Standards Regulatory Support Document (RSD),\u00e2\u0080\u009d Office of Mobile Sources, U.S.\\nEnvironmental Protection Agency, Ann Arbor, MI. April 1997.\\n6. \u00e2\u0080\u009cFuel Oil and Kerosene Sales,\u00e2\u0080\u009d DOE/EIA-0380, Energy Information Administration, U.S. Department of Energy,\\nWashington, DC. 1996.\\n7. Barnard, W.R., C. Walvoord, S. Nizich, R.L. Tooly, and D. Solomon, \u00e2\u0080\u009cIncorporation of State Emissions Data into the\\nNational Emission Trends Data Base,\u00e2\u0080\u009d presented at the Air Waste Management Association Specialty Conference,\\nThe Emission Inventory: Regional Strategies for the Future Raleigh, NC. October 1999.\\n8. \u00e2\u0080\u009cNational Air Pollutant Emission Trends Procedures Document, Current Methods for Historic and Projection Year\\nEmission Estimates,\u00e2\u0080\u009d Office of Air Quality Planning and Standards, U.S. Environmental Protection Agency, Research\\nTriangle Park, NC. Draft, in preparation.\\n9. \u00e2\u0080\u009cEPA EGAS EDFS-14 Multi-Region County Models,\u00e2\u0080\u009d Nine DOS Models Covering the U.S., Last History Year 1996,\\nRegional Economic Models, Inc., CD-ROM. February 18, 1999.\\n10. \u00e2\u0080\u009cRegional Projections to 2045,\u00e2\u0080\u009d Volumes 1, 2, and 3, Bureau of Economic Analysis, U.S. Department of Commerce,\\nWashington DC. July 1995.\\n11. \u00e2\u0080\u009cAnnual Energy Outlook 1999, with Projections through 2020,\u00e2\u0080\u009d DOE/EIA-0383(99), Office of Integrated Analysis and\\nForecasting, Energy Information Administration, U.S. Department of Energy. December 1998.\\n12. \u00e2\u0080\u009cEmission Inventory Procedural Manual, Volume III: Methods for Assessing Area Source Emissions,\u00e2\u0080\u009d California EPA:\\nAir Resources Board. 1994.\\n13. \u00e2\u0080\u009cThe Benefits and Costs of the Clean Air Act 1990 to 2010,\u00e2\u0080\u009d EPA Report to Congress, EPA-410-R-99-001, U.S.\\nEnvironmental Protection Agency. 1999.\\n14. \u00e2\u0080\u009cForest Statistics of the United States, 1987,\u00e2\u0080\u009d USFS publication, PNW-RB-168, U.S. Forest Service. September 1989.\\n15. \u00e2\u0080\u009cDevelopment and Use of Heavy-Duty NO x Defeat Device Emission Effects for MOBILE5 and MOBILE 6,\u00e2\u0080\u009d EPA420-\\nP-99-030, U.S. Environmental Protection Agency. October 1999.\\n5-10 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0110.jp2"}, "111": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 5-1. Emission Estimation Methods That Have Changed Since the Last Report\\nYear of Inventory\\nPollutant\\nCategory\\nMethodology Change*\\n1990\\nCO, VOC, NO,\\nPrimarily nonutility point\\nsources and 17 states\\nworth of area sources\\nA combination of Ozone Transport Assessment Group (OTAG), Grand\\nCanyon Visibility Transport Commission Inventory (GCVTC), and\\nAerometric Information Retrieval System (AIRS) data was added to\\ninventory, replacing some units but primarily just adding more units.\\n(Ozone season daily data received was developed into annual data).\\n1990\\nF*Mio EM 2 5, S0 2\\nAs above\\nState data received as above was augmented with PM and S0 2 data\\nthrough an S0 2 and PM to NO, uncontrolled emission factor ratio.\\n1991-1995\\nAll but Pb\\nPrimarily nonutility point\\nsources and 17 states\\nworth of area sources\\nNAPAP, AIRS data, GCVTC and Grand Canyon projections from the\\n1990 inventory using Bureau of Economic Analysis (BEA) growth\\nindicators.\\n1990\\nAll but Pb\\non-road mobile\\n1990, 1995, 1996 use state-supplied MOBILE model inputs where\\napplicable. See Reference 1 for a list of States supplying model inputs.\\n1990\\nAll but Pb\\non-road mobile\\nUsed state supplied vehicle miles traveled (VMT) where applicable. See\\nReference 1 for a list of States providing VMT.\\n1985-1989\\nAll but Pb\\nchemical and allied\\nRemoved rule effectiveness from pre-1990 chemical and allied product\\nemissions.\\n1985-1994\\nNO x\\nutilities\\nUsed NO x emission rates from Acid Rain Division (ARD) instead of AP-42\\nemission factors.\\n1994-1998\\nNO x S0 2\\nutilities\\nBased Phase 1 units on CEM data from ARD, remaining units are from\\nDOE767 survey data (small amount of units).\\n1996\\nAll but Pb\\nnonutility point (35 states)\\nand area sources (14\\nstates)\\nAdded state-supplied data directly received from states or retrieved from\\nAIRS as part of the PEI inventory effort, as directed by the states.\\n5 State submittals were select cities only.\\n1997-1998\\nAll but Pb\\nnonutility point and area\\nsources\\nProjected through 1998 based on the 1996 PEI enhanced database using\\nEGAS derived growth factors and BEA growth factors where applicable.\\n1970, 1975, 1980\\nAll but Pb\\nnon-road sources\\nGenerated national-level nonroad emission estimates based on category-\\nspecific ratios of 1996 NON ROAD model outputs to previous year national\\nestimates.\\n1985-1998\\nAll but Pb\\nnon-road sources\\nRan the beta version of the NONROAD model for all counties in U.S. for\\n1996. Used the NONROAD model to calculate national emissions for the\\nother years and then used SCC-specific ratios for the other years relative\\nto 1996 (year in question/1996) to determine county-level estimates.\\n1985-1998\\nAll but Pb\\nnon-road sources\\nFor commercial marine diesel, EPA\u00e2\u0080\u0099s OTAQ provided revised national\\nVOC, NO x CO, and PM emission estimates for commercial marine diesel\\nengines. National estimates were distributed to counties using the\\ngeographic distribution in the existing NET.\\n1990-1998\\nAll but Pb\\nMiscellaneous-agric.\\nforestry\\nRevised allocation of Census of Agriculture activity data between the\\n1990 and 1997 census: used agricultural surrogates instead of economic\\nsurrogates.\\n1990-1998\\nPM\\nMiscellaneous -agric.\\ncrops\\nBegan using tillage activity data using the Conservation Technology\\nInformation Center, Purdue University, data, and also changed silt value\\nmethodology from 1990 onward.\\n1989-1998\\nPM\\nMiscellaneous-managed\\nburning\\nBased on USDA Forest Service inventory of PM from prescribed burning.\\nPublic percentage of acres burned projected from 1990 using national-\\nlevel growth factor developed from total U.S. acres burned, while private\\nportion held constant.\\n1990-1998\\nPM\\nMiscellaneous\\n-construction\\nChanged the emission factor in 1990: changed from using a former AP-42\\nvalue to using latest AP-42 findings report: \u00e2\u0080\u009cImprovement of Specific\\nEmission Factors\u00e2\u0080\u009d change occurred in Trends year 1997.\\n1990-1998\\nPM\\npaved roads\\nThe rain correction factor in the paved road equation was reduced by 50\\npercent for the years 1990 onward due to uncertainty associated with the\\nactual reduction in emissions due to precipitation on paved road surfaces.\\n1990-1998\\nAll but Pb\\nstructural fires\\nFor non-OTAG States, revised 1990 and 1996 emissions based on new\\nloading factor value. Projected all States using EGAS regression\\nequations, which relate State-level population to the amount of material\\nburned in structure fires.\\nFor a list of specific\\ndata sources usee\\nfor each State, please see Section 4.1 of reference 8.\\n5.0 National Criteria Pollutant Estimation Methodologies 5-11", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0111.jp2"}, "112": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 5-2. Point and Area Source Data Submitted\\nPoint Sources\\nArea Sources\\nState\\nSource\\nAdjustments to Point Source Data\\nSource\\nAdjustments to Area Source Data\\nAlabama\\nPEI\\nPEI\\nBirmingham NAA Only\\nAlabama\\nOTAG\\nBackcast to 1990 using BEA. Average\\nSummer Day estimated using\\nmethodology described.\\nNAPAP\\nArizona\\nNAPAP\\nNAPAP\\nArkansas\\nOTAG\\nAverage Summer Day estimated using\\ndefault temporal factors.\\nNAPAP\\nCalifornia\\nPEI\\nPEI\\nColorado\\nPEI\\nNAPAP\\nConnecticut\\nPEI\\nPEI\\nDelaware\\nPEI\\nPEI\\nFlorida\\nPEI\\nOTAG\\nAdded Non-road emissions estimates from\\nInt. Inventory to Jacksonville (Duval County).\\nGeorgia\\nPEI\\nOnly Atlanta not statewide\\nPEI\\nOnly Atlanta not statewide\\nGeorgia\\nOTAG\\nAverage Summer Day estimated using\\ndefault temporal factors.\\nOTAG\\nIdaho\\nNAPAP\\nPEI data submitted but not incorporated\\nNAPAP\\nPEI data submitted but not incorporated into\\ninto NET inventory.\\nNET inventory.\\nIllinois\\nPEI\\nOTAG\\nIndiana\\nPEI\\nPEI\\nIowa\\nNAPAP\\nNAPAP\\nKansas\\nPEI\\nNAPAP\\nKentucky\\nPEI\\nOTAG\\nLouisiana\\nPEI\\nPEI\\nMaine\\nPEI\\nOTAG\\nMaryland\\nPEI\\nPEI\\nMassachusetts\\nPEI\\nNAPAP\\nMichigan\\nPEI\\nOTAG\\nMinnesota\\nOTAG\\nAverage Summer Day estimated using\\nmethodology described above.\\nNAPAP\\nMississippi\\nNAPAP\\nNAPAP\\nMissouri\\nPEI\\nOnly partial state.\\nPEI\\nSt. Louis NAA Only\\nMissouri\\nOTAG\\nBackcast to 1990 using BEA. Average\\nSummer Day estimated using\\nmethodology described above.\\nMontana\\nPEI\\nNAPAP\\nNebraska\\nPEI\\nNAPAP\\nNevada\\nNAPAP\\nNAPAP\\nNew Hampshire\\nPEI\\nOTAG\\nNew Jersey\\nOTAG\\nOTAG\\nNew Mexico\\nNAPAP\\nNAPAP\\nNew York\\nOTAG\\nOTAG\\nNorth Carolina\\nPEI\\nOTAG\\nAverage Summer Day estimated using\\ndefault temporal factors.\\nNorth Dakota\\nPEI\\nNAPAP\\nOhio\\nOTAG\\nAverage Summer Day estimated using\\nOTAG\\nAssigned SCCs and converted from kgs to\\nmethodology described above.\\ntons. NO x and CO from Int. Inventory added\\nto Canton, Dayton and Toledo counties.\\nOklahoma\\nPEI\\nPEI\\n5-12 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0112.jp2"}, "113": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 5-2 (continued)\\nPoint Sources\\nArea Sources\\nState\\nSource\\nAdjustments to Point Source Data\\nSource\\nAdjustments to Area Source Data\\nOregon\\nGCVTC\\nGCVTC\\nPennsylvania\\nPEI\\nAllegheny and Philadelphia Counties\\nOnly\\nPEI\\nAllegheny and Philadelphia Counties Only\\nPennsylvania\\nOTAG\\nOTAG\\nNon-road emissions submitted were county\\ntotals. Non-road emissions distributed to\\nspecific SCCs based on Int. Inventory\\nRhode Island\\nOTAG\\nOTAG\\nSouth Carolina\\nPEI\\nNAPAP\\nSouth Dakota\\nPEI\\nNAPAP\\nTennessee\\nOTAG\\nAverage Summer Day estimated using\\nOTAG\\nNo non-road data submitted. Non-road\\ndefault temporal factors.\\nemissions added from Int. Inventory.\\nTexas\\nPEI\\nPEI\\nNAAs Only (Houston, Beaumont, Dallas, El\\nPaso)\\nUtah\\nNAPAP\\nNAPAP\\nVermont\\nPEI\\nOTAG\\nVirginia\\nPEI\\nPEI\\nWashington\\nPEI\\nPEI\\nWest Virginia\\nPEI\\nOTAG\\nWisconsin\\nPEI\\nOTAG\\nWyoming\\nNAPAP\\nNAPAP\\nNOTE(S): Year of Inventory is 1996 for PEI, 1990 for OTAG and GCVTC, and 1985 for NAPAP\\n5.0 National Criteria Pollutant Estimation Methodologies 5-13", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0113.jp2"}, "114": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 5-3. Utility Boiler Emissions Data Sources for NO x and S0 2 by Year\\nYear\\nNO x\\nCsl\\nO\\nif)\\n1985\\nOverlaid Acid Rain Division (ARD) coal NO x\\nrate calculations when possible\\nNADBV311 data\\n1986\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1987\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1988\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1989\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1990\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1991\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1992\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1993\\nOverlaid ARD coal NO x rate calculations\\nwhen possible\\nCalculated from EIA-767 data\\n1994\\nOverlaid ARD coal NO x rate calculations\\nwhen possible; overlaid ETS/CEM data\\nwhen possible\\nCalculated from EIA-767 data\\n1995\\nOverlaid ETS/CEM data when possible\\nOverlaid ETS/CEM data when possible\\n1996\\nOverlaid ETS/CEM data when possible\\nOverlaid ETS/CEM data when possible\\n1997\\nOverlaid ETS/CEM data when possible\\nOverlaid ETS/CEM data when possible\\n1998\\nGrew from 1997 data and overlaid ETS/CEM\\ndata when possible\\nGrew from 1997 data and overlaid\\nETS/CEM data when possible\\n5-14 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0114.jp2"}, "115": {"fulltext": "Figure 5-1. States Submitting Point and/or Area Source Data\\nfor the 1996 PEI\\nNational Air Pollutant Emission Trends, 1990-1998\\n5.0 National Criteria Pollutant Estimation Methodologies 5-15\\nJ To Be Processed FY2000\\nAllegheny and Philadelphia Counties Processed", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0115.jp2"}, "116": {"fulltext": "[This page intentionally left blank.]", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0116.jp2"}, "117": {"fulltext": "Chapter 6.0 Biogenic Emissions\\n6.1 WHAT EMISSIONS DATA DOES EPA\\nPRESENT IN THIS CHAPTER?\\nThis chapter presents preliminary biogenic volatile\\norganic compound (VOC) and nitric oxide (NO) emissions for\\n1988, 1990, 1991, 1995, 1996, and 1997. Estimates for 1998\\nare not available because the United States (U.S.)\\nEnvironmental Protection Agency (EPA) did not have the\\nresources to develop biogenic estimates for that year. The\\n1998 estimates will be included in the 1999 Trends report.\\nTables 6-1 and 6-2 show VOC and NO emissions,\\nrespectively. Tables 2-1, A-2, and A-3 do not contain the\\nbiogenic emission estimates because EPA only tracks\\nanthropogenic emissions for regulatory purposes.\\n6.2 HOW WERE THESE EMISSIONS\\nGENERATED?\\nEPA calculated the biogenic emissions for 1988, 1991,\\n1995,1996, and 1997 using the Biogenic Emissions Inventory\\nSystem Version 2 (BEIS2). 1 2,3 EPA used a slightly different\\nversion of BEIS2 to generate the 1990 estimates.\\n6.3 WHY DO THESE EMISSIONS VARY?\\nDifferences in climatology (i.e., temperature and cloud\\ncover) and land use strongly affect biogenic emissions.\\n6.4 HOW DOES TEMPERATURE AFFECT\\nEMISSIONS?\\nAnnual emissions correlate very strongly with changes in\\nannual temperature patterns. The highest emissions levels\\noccur in the summer when temperatures rise the highest. An\\nincrease of 10\u00c2\u00b0C can cause over a two-fold increase in VOC\\nand NO emissions. Tables 6-3 and 6-4 show the seasonal\\nallocation of VOC and NO emissions, respectively.\\n6.5 HOW DOES LAND USE AFFECT\\nEMISSIONS?\\nVariations in land use can greatly affect spatial variation\\nin biogenic emissions densities. In the southern United States\\nand Missouri, large areas of oak trees show high VOC\\ndensities, while in the midwestern United States, areas of\\nfertilized crop lands show relatively high densities of NO.\\nFigures 6-1 and 6-2 show the spatial variation in biogenic\\nemission densities across the United States.\\n6.6 WHAT IS THE UNCERTAINTY\\nASSOCIATED WITH THESE\\nESTIMATES?\\nThese estimates have an uncertainty factor of a maximum\\nof two. However, biogenic emissions research continues to be\\nquite active, and EPA expects improvements in these emission\\nestimates in the next few years.\\n6.7 REFERENCES\\n1. Birth, T., \u00e2\u0080\u009cUser\u00e2\u0080\u0099s Guide to the PC Version of the Biogenic Emissions Inventory System (PC-BEIS2),\u00e2\u0080\u009d EPA-600/R-95-091,\\nU.S. Environmental Protection Agency, Research Triangle Park, NC. 1995.\\n2. Geron, C., A. Guenther, and T. Pierce, \u00e2\u0080\u009cAn Improved Model for Estimating Emissions of Volatile Organic Compounds from\\nForests in the Eastern United States,\u00e2\u0080\u009d Journal of Geophysical Research vol. 99, pp. 12773-12791. 1994.\\n3. Williams, E\u00e2\u0080\u009e A. Guenther, and F. Fehsenfeld, \u00e2\u0080\u009cAn Inventory of Nitric Oxide Emissions from Soils in the United States,\u00e2\u0080\u009d\\nJournal of Geophysical research, vol. 97, pp. 7511-7519. 1992.\\n6.0 Biogenic Emissions 6-1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0117.jp2"}, "118": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 6-1. Biogenic Volatile Organic Compound Emissions by State\\n(thousand short tons)\\nState\\n1988\\n1990\\n1991\\n1995\\n1996\\n1997\\nAlabama\\n1,826\\n2,114\\n1,852\\n1,937\\n1,597\\n1,579\\nArizona\\n535\\n542\\n517\\n548\\n591\\n545\\nArkansas\\n1,837\\n1,852\\n1,476\\n1,741\\n1,472\\n1,517\\nCalifornia\\n1,815\\n1,778\\n1,711\\n1,794\\n2,125\\n1,623\\nColorado\\n889\\n748\\n817\\n826\\n878\\n786\\nConnecticut\\n81\\n68\\n74\\n81\\n63\\n68\\nDelaware\\n25\\n19\\n24\\n26\\n20\\n21\\nDistrict of Columbia\\n1\\n1\\n1\\n1\\n0\\n1\\nFlorida\\n1,352\\n1,513\\n1,246\\n1,436\\n1,255\\n1,307\\nGeorgia\\n1,666\\n1,958\\n1,609\\n1,721\\n1,454\\n1,405\\nIdaho\\n854\\n810\\n764\\n706\\n726\\n726\\nIllinois\\n283\\n227\\n257\\n244\\n191\\n187\\nIndiana\\n237\\n185\\n227\\n218\\n165\\n157\\nIowa\\n141\\n95\\n103\\n112\\n89\\n93\\nKansas\\n154\\n140\\n133\\n118\\n116\\n119\\nKentucky\\n677\\n575\\n648\\n636\\n496\\n464\\nLouisiana\\n1,291\\n1,403\\n1,043\\n1,367\\n1,125\\n1,187\\nMaine\\n599\\n567\\n621\\n622\\n531\\n453\\nMaryland\\n164\\n132\\n155\\n169\\n127\\n135\\nMassachusetts\\n140\\n107\\n129\\n140\\n109\\n119\\nMichigan\\n581\\n422\\n548\\n533\\n394\\n408\\nMinnesota\\n729\\n519\\n612\\n636\\n533\\n502\\nMississippi\\n1,662\\n1,801\\n1,450\\n1,642\\n1,402\\n1,419\\nMissouri\\n1,472\\n1,222\\n1,298\\n1,267\\n1,056\\n1,045\\nMontana\\n912\\n729\\n781\\n666\\n716\\n680\\nNebraska\\n95\\n79\\n81\\n78\\n72\\n77\\nNevada\\n152\\n140\\n142\\n135\\n158\\n126\\nNew Hampshire\\n168\\n147\\n163\\n171\\n137\\n286\\nNew Jersey\\n130\\n115\\n124\\n132\\n103\\n107\\nNew Mexico\\n505\\n533\\n499\\n531\\n544\\n440\\nNew York\\n350\\n303\\n328\\n361\\n280\\n290\\nNorth Carolina\\n1,072\\n1,194\\n1,002\\n1,110\\n908\\n882\\nNorth Dakota\\n69\\n49\\n51\\n48\\n46\\n50\\nOhio\\n270\\n211\\n243\\n259\\n197\\n183\\nOklahoma\\n1,013\\n1,016\\n864\\n887\\n836\\n811\\nOregon\\n1,066\\n1,118\\n1,002\\n1,114\\n1,087\\n1,075\\nPennsylvania\\n594\\n510\\n560\\n642\\n460\\n473\\nRhode Island\\n24\\n18\\n21\\n24\\n18\\n20\\nSouth Carolina\\n738\\n886\\n652\\n755\\n626\\n632\\nSouth Dakota\\n142\\n103\\n113\\n104\\n102\\n102\\nTennessee\\n1,063\\n1,022\\n1,010\\n997\\n817\\n781\\nTexas\\n2,711\\n2,864\\n2,244\\n2,649\\n2,481\\n2,431\\nUtah\\n407\\n374\\n353\\n345\\n410\\n324\\nVermont\\n102\\n91\\n100\\n106\\n88\\n90\\nVirginia\\n911\\n886\\n850\\n917\\n728\\n714\\nWashington\\n685\\n780\\n650\\n801\\n735\\n763\\nWest Virginia\\n510\\n420\\n473\\n492\\n383\\n368\\nWisconsin\\n648\\n450\\n516\\n541\\n412\\n398\\nWyoming\\n505\\n387\\n397\\n358\\n396\\n223\\nNational\\n33,852\\n33,224\\n30,536\\n32,742\\n29,254\\n28,194\\nNOTE: The sums of States may not equal National total due to rounding.\\n6-2 6.0 Biogenic Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0118.jp2"}, "119": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 6-2. Biogenic Nitric Oxide Emissions by State\\n(thousand short tons)\\nState\\n1988\\n1990\\n1991\\n1995\\n1996\\n1997\\nAlabama\\n14\\n19\\n14\\n14\\n14\\n14\\nArizona\\n55\\n51\\n53\\n55\\n58\\n55\\nArkansas\\n19\\n21\\n19\\n19\\n18\\n18\\nCalifornia\\n42\\n40\\n42\\n42\\n44\\n41\\nColorado\\n39\\n35\\n38\\n38\\n39\\n35\\nConnecticut\\n1\\n1\\n1\\n1\\n1\\n1\\nDelaware\\n2\\n2\\n2\\n2\\n2\\n2\\nDistrict of Columbia\\n0\\n0\\n0\\n0\\n0\\n0\\nFlorida\\n22\\n29\\n22\\n22\\n22\\n22\\nGeorgia\\n19\\n29\\n20\\n20\\n19\\n19\\nIdaho\\n25\\n23\\n24\\n24\\n24\\n24\\nIllinois\\n90\\n84\\n90\\n86\\n81\\n82\\nIndiana\\n49\\n48\\n51\\n49\\n46\\n46\\nIowa\\n93\\n82\\n90\\n87\\n81\\n85\\nKansas\\n91\\n87\\n91\\n85\\n83\\n85\\nKentucky\\n19\\n20\\n20\\n19\\n18\\n18\\nLouisiana\\n19\\n20\\n19\\n19\\n19\\n19\\nMaine\\n3\\n3\\n3\\n3\\n2\\n2\\nMaryland\\n6\\n6\\n6\\n6\\n6\\n6\\nMassachusetts\\n1\\n1\\n1\\n1\\n1\\n1\\nMichigan\\n25\\n25\\n26\\n25\\n23\\n24\\nMinnesota\\n58\\n52\\n56\\n54\\n50\\n53\\nMississippi\\n19\\n22\\n19\\n19\\n19\\n18\\nMissouri\\n44\\n42\\n44\\n42\\n40\\n40\\nMontana\\n60\\n49\\n57\\n53\\n52\\n50\\nNebraska\\n91\\n83\\n90\\n86\\n80\\n85\\nNevada\\n46\\n38\\n44\\n44\\n47\\n41\\nNew Hampshire\\n1\\n1\\n1\\n1\\n1\\n2\\nNew Jersey\\n2\\n2\\n2\\n2\\n2\\n2\\nNew Mexico\\n62\\n59\\n61\\n64\\n65\\n56\\nNew York\\n17\\n19\\n18\\n18\\n17\\n17\\nNorth Carolina\\n21\\n26\\n22\\n21\\n20\\n20\\nNorth Dakota\\n51\\n42\\n48\\n44\\n43\\n47\\nOhio\\n36\\n36\\n37\\n35\\n33\\n33\\nOklahoma\\n35\\n37\\n35\\n34\\n34\\n33\\nOregon\\n24\\n22\\n23\\n23\\n23\\n23\\nPennsylvania\\n19\\n21\\n20\\n20\\n18\\n19\\nRhode Island\\n0\\n0\\n0\\n0\\n0\\n0\\nSouth Carolina\\n10\\n16\\n11\\n11\\n10\\n10\\nSouth Dakota\\n62\\n53\\n60\\n56\\n52\\n56\\nTennessee\\n17\\n18\\n18\\n17\\n16\\n16\\nTexas\\n199\\n203\\n199\\n202\\n206\\n195\\nUtah\\n28\\n25\\n27\\n28\\n29\\n23\\nVermont\\n2\\n2\\n2\\n2\\n2\\n2\\nVirginia\\n10\\n12\\n10\\n10\\n9\\n9\\nWashington\\n15\\n15\\n14\\n15\\n15\\n15\\nWest Virginia\\n4\\n4\\n4\\n4\\n3\\n3\\nWisconsin\\n36\\n34\\n35\\n35\\n32\\n33\\nWyoming\\n39\\n40\\n36\\n35\\n35\\n28\\nNational\\n1,638\\n1,596\\n1,628\\n1,591\\n1,553\\n1,529\\nNOTE: The sums of States may not equal National total due to rounding.\\n6.0 Biogenic Emissions 6-3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0119.jp2"}, "120": {"fulltext": "National Air Pollutant Emission Trends 1900 1998\\nTable 6-3. Biogenic Volatile Organic\\nCompound Seasonal Allocation,\\n1988 to 1996 (percentages)\\nYear\\nWinter\\nSprinq\\nSummer\\nAutumn\\n1988\\n3\\n18\\n61\\n18\\n1990\\n4\\n17\\n57\\n22\\n1991\\n3\\n21\\n62\\n14\\n1995\\n3\\n18\\n59\\n19\\n1996\\n3\\n19\\n58\\n20\\nTable 6-4. Biogenic Nitric Oxide Seasonal\\nAllocation, 1988 to 1996\\n(percentages)\\nYear\\nWinter\\nSprinq\\nSummer\\nAutumn\\n1988\\n11\\n23\\n42\\n24\\n1990\\n15\\n21\\n39\\n25\\n1991\\n12\\n24\\n40\\n23\\n1995\\n12\\n22\\n41\\n24\\n1996\\n12\\n23\\n41\\n24\\n6-4 6.0 Biogenic Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0120.jp2"}, "121": {"fulltext": "Figure 6-1. Density Map of NITROGEN OXIDES 1997\\nBiogenic Emissions by County\\nNational Air Pollutant Emission Trends, 1990-1998\\nO\\nA\\nn\\n6.0 Biogenic Emissions 6-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0121.jp2"}, "122": {"fulltext": "National Air Pollutant Emission Trends, 1990-1998\\no\\nA\\n6-6 6.0 Biogenic Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0122.jp2"}, "123": {"fulltext": "Chapter 7.0 Hazardous Air Pollutants\\n7.1 WHAT INFORMATION IS PRESENTED\\nIN THIS CHAPTER?\\nThis chapter discusses hazardous air pollutants (HAPs).\\nHAPs are commonly referred to as \u00e2\u0080\u009cair toxics\u00e2\u0080\u009d or \u00e2\u0080\u009ctoxic air\\npollutants.\u00e2\u0080\u009d They are pollutants known to cause or suspected\\nof causing cancer or other serious human health effects or\\necosystem damage. Section 112 of the Clean Air Act (CAA)\\nnow lists 188 pollutants or chemical groups as HAPs and\\ntargets stationary sources of these pollutants for regulation. 1\\nExamples of air toxics include heavy metals like mercury and\\nchromium; organic chemicals like benzene, 1,3-butadiene,\\nperchloroethylene, dioxins, and polycyclic organic matter.\\nHAPs are emitted from literally thousands of sources\\nincluding: point sources (such as electric power utilities or\\nindustrial manufacturers), smaller area sources (such as\\nneighborhood dry cleaners or service stations), and mobile\\nsources (such as automobiles or airplanes). Adverse effects to\\nhuman health and the environment due to HAPs can result\\nfrom exposure to air toxics from individual facilities, exposure\\nto mixtures of pollutants found in urban settings, or exposure\\nto pollutants emitted from distant sources that are transported\\nthrough the atmosphere over regional, national or even global\\nairsheds. In addition to breathing air contaminated with air\\ntoxics, people can also be exposed to some HAPs through\\nother pathways such as through the ingestion of contaminated\\nfood from waters polluted from the deposition of HAPs from\\nthe air to water bodies (e.g. fish contaminated with mercury).\\n7.2 WHAT ARE THE HEALTH AND\\nENVIRONMENTAL EFFECTS OF HAPs?\\nMost of the information on potential health effects of\\nHAPs is derived from experimental animal data and studies of\\nexposed workers. The different health effects which may be\\ncaused by HAPs include cancer, neurological, cardiovascular,\\nand respiratory effects, effects on the liver, kidney, immune\\nsystem, and reproductive system, and effects on fetal and child\\ndevelopment. More than half of the 188 HAPs have been\\nclassified by the United States (U.S.) (EPA) as \u00e2\u0080\u009cknown,\u00e2\u0080\u009d\\n\u00e2\u0080\u009cprobable,\u00e2\u0080\u009d or \u00e2\u0080\u009cpossible\u00e2\u0080\u009d human carcinogens. Known human\\ncarcinogens are those that have been demonstrated to cause\\ncancer in humans. Probable and possible human carcinogens\\ninclude chemicals that we are less certain cause cancer in\\npeople, yet for which laboratory animal testing or limited\\nhuman data indicates carcinogenic effects.\\nSome HAPs pose particular hazards to people of a certain\\nage or stage in life (e.g., young children, adolescents, adults,\\nor elderly people). Available data suggest that about a third of\\nHAPs (e.g., mercury) may be developmental or reproductive\\ntoxicants in humans. This means that exposure during the\\ndevelopment of a fetus or young child may prevent normal\\ndevelopment into a healthy adult. Other such critical\\nexposures may affect the ability to conceive or give birth to a\\nhealthy child. Toxic air pollutants can have a variety of\\nenvironmental impacts in addition to the threats they pose to\\nhuman health. Animals, like humans, may experience health\\nproblems if they breathe sufficient concentrations of HAPs\\nover time, or ingest HAPs through contaminated food (e.g.\\nfish).\\n7.3 WHY ARE AIR TOXICS INVENTORIES\\nNEEDED?\\nSection 112 of the CAA added a new approach to the\\nregulation of HAPs, consisting of two phases. The first\\nrequires the development of technology-based emissions\\nstandards for sources emitting the 188 HAPs. The second\\nphase requires the evaluation of any remaining problems or\\nrisks, and development of additional regulations to address\\nsources of those problems, as needed. In implementing the\\nSection 112 provisions, EPA has collected information that\\nhelps characterize air toxics emissions. Emission inventories\\nare a key component of this characterization process and also\\nprovide important information with which to monitor progress\\ntowards meeting the emission reduction goals.\\n7.3.1 Which EPA Regulatory Activities Use\\nHAP Emission Inventories?\\nPhase One\\nUnder Section 112 of the CAA, the first phase of\\nrequirements is comprised of the technology-based standards,\\nknown as maximum achievable control technology (MACT)\\nand generally achievable control technology (GACT)\\nregulations. All large stationary sources, or \u00e2\u0080\u009cmajor\u00e2\u0080\u009d sources,\\nof the 188 HAPs must be addressed by such regulations, as\\nwell as the smaller, \u00e2\u0080\u009carea\u00e2\u0080\u009d stationary sources found to produce\\nsignificant risk or emit priority pollutants such as those\\nHazardous Air Pollutants 7-1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0123.jp2"}, "124": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nidentified under Section 112(c)(6) or the Integrated Urban Air\\nToxics Strategy described below. Some combustion sources,\\nsuch as municipal waste combustors, and medical waste\\nincinerators are regulated under equivalent requirements in\\nSection 129. The purpose of this technology-based approach\\nis to use available control technologies, changes in work\\npractices, or pollution prevention methods to get emission\\nreductions for as many of the HAPs as possible. It is expected\\nthat the MACT and GACT standards will reduce a majority of\\nthe HAP emissions and, in turn, reduce risks from regulated\\nsources. This initial phase has generated emissions data for\\nseveral industries as they are studied in the MACT and GACT\\nregulatory development process as well as other CAA\\nprovisions that require EPA to evaluate emissions of utility\\nindustry HAP emissions, mercury, and other specific air\\ntoxics. These requirements are summarized below.\\nUtility Study, Section 112(n)(l)(A) requires a report to\\nCongress on the \u00e2\u0080\u009chazards to public health reasonably\\nanticipated to occur as a result of the emissions of electric\\nutility steam generating units.\u00e2\u0080\u009d\\nMercury Study, Section 112(n)(l)(B) requires a report\\nto Congress regarding emissions of mercury that \u00e2\u0080\u009cshall\\nconsider the rate and mass of such emissions, the health\\nand environmental effects of such emissions...\u00e2\u0080\u009d\\nSpecific Pollutants, Section 112(c)(6) requires a \u00e2\u0080\u009clist of\\ncategories and subcategories of sources assuring that\\nsources accounting for not less that 90 percent of the\\naggregate emissions of each pollutant are subject to\\nstandards.\u00e2\u0080\u009d This provision applies to seven specific\\nHAPs: alkylated lead (Pb) compounds, mercury, dioxins,\\npolycyclic organic matter (POM), hexachlorobenzene,\\npolychlorinated biphenyls (PCBs) and furans.\\nArea Source Program, Section 112(c)(3) requires that\\nthe \u00e2\u0080\u009cemissions of the 30 hazardous air pollutants that\\npresent the greatest threat to public health in the largest\\nnumber of urban areas are subject to regulation.\u00e2\u0080\u009d\\nImplementation of Section 112 through Title V of the\\nCAA requires the Administrator to perform an oversight\\nrole with respect to State issued permits, including\\npermits issued to major sources of HAP emissions. In\\norder to determine whether that program is being\\nappropriately and lawfully administrated by the States\\nwith respect to major HAP sources, a HAP emission\\ninventory is necessary. States are developing programs to\\nregulate HAPs and their Title V programs must include\\npermits for all HAP sources emitting major quantities of\\nHAPs (10 tons of one HAP or 25 tons of multiple HAPs\\nper year). Thus the Administrator believes maintaining an\\ninventory of such sources is necessary and appropriate.\\nPhase Two:\\nAfter application of these technology-based standards and\\nstudies, in the second phase, the CAA requires strategies and\\nprograms for evaluating remaining risks and effects and\\nensuring that the overall program has achieved sufficient\\nimprovement. This phase will be implemented through\\nprograms that evaluate these remaining risk and effects. Such\\nprograms are described below.\\nIntegrated Urban Air Toxics Strategy responds to the\\nrequirements of Sections 112(k) and 112(c)(3) of the\\nCAA, and also reflects activities to control mobile source\\nemissions required under section 202(1). The goals of the\\nIntegrated Urban Air Toxics Strategy consist of the\\nfollowing: 1) attain a 75-percent reduction in incidence of\\ncancer attributable to exposure to HAPs emitted by\\nstationary sources; 2) attain a substantial reduction in\\npublic health risks posed by HAP emissions from area\\nsources; and 3) address disproportionate impacts of air\\ntoxics hazards across urban areas. The Integrated Urban\\nAir Toxics Strategy was finalized in July 19, 1999\\nFederal Register. 2\\nResidual Risk, Section 112(f requires an assessment of\\nthe residual risk after certain Section 112 standards are\\nimplemented. Residual risk standards are to be developed\\nas determined necessary eight years after promulgation of\\nthese standards.\\nThe Great Waters Program, Section 112(m) requires\\nEPA to identify \u00e2\u0080\u009cthe extent of atmospheric deposition of\\nhazardous air pollutants\u00e2\u0080\u009d to specified water bodies,\\n\u00e2\u0080\u009cevaluate any adverse effects to pubic health or the\\nenvironment caused by such deposition,\u00e2\u0080\u009d and determine\\nwhether additional regulations are warranted.\\nInventories play a crucial role in each of these programs\\nas the inventory information is used to evaluate current\\nemissions, emissions reductions achieved, and identify the\\nnumerous source categories which emit specific pollutants.\\nInventories are an important tool in evaluating the risk\\nreductions goals for the Integrated Urban Air Toxics Strategy.\\nIn addition, EPA is also using information from inventories to\\nplan what future work might need to be done. For more\\ninformation on Section 112 programs refer to the EPA\u00e2\u0080\u0099s\\nwebsite at http://www.epa.gov/ttn/uatw.html.\\n7.4 WHAT IS EPA\u00e2\u0080\u0099S PLAN TO GATHER\\nTHE NECESSARY TOXICS DATA?\\nAs the EPA began working to meet the air toxics\\nrequirements of the CAA, it became clear that there was a\\nstrong need for a central source of air toxics emissions and\\ninventory data from which to conduct the analyses required by\\nthe CAA, and to have a place to centrally store and share the\\n7-2 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0124.jp2"}, "125": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\ndata being generated through various programs. The increased\\navailability of air toxics emissions data will assist EPA\\nprogram offices and other agencies that use emissions data to\\nevaluate state, local, or tribal air pollution related issues. Air\\ntoxics data needs vary from national estimates of emissions to\\nregional estimates, county-level estimates, and facility-specific\\nestimates, and even down to process-specific estimates. Thus,\\nin 1993, EPA began development of a national air toxics\\ninventory data base now referred to as the National Toxics\\nInventory (NTI).\\n7.5 WHAT IS THE NTI?\\nThe NTI is a central repository of estimated emissions for\\nthe 188 HAPs for all anthropogenic (manmade) sources.\\n7.5.1 How was the NTI Developed?\\nThe national estimates of the HAPs included in the NTI\\nto date were calculated using existing information; no source\\ntesting or industry surveys were conducted specifically for the\\npurposes of generating the NTI. Existing emission inventory\\ndata were obtained from a variety of state and local data bases\\nand EPA programs (such as the Toxics Release Inventory\\n(TRI), standards development programs, and other studies\\nrequired by the CAA such as the Utility Study). Sometimes\\nemissions information is available from direct measurement of\\nemissions at a given source. However, for logistical and\\nfinancial reasons direct measurement, or stack testing, cannot\\nbe performed at every source and instead, most inventory data\\nare developed via various estimation techniques.\\nMany of the national emissions estimates in the NTI\\n(primarily for area and mobile sources) were developed by\\napplying an emission factor, which is an emissions estimate\\nbased on test data and correlated to some other process\\nactivity. For example an emissions factor could be expressed\\nin terms of grams emitted per ton of coal burned or per vehicle\\nmile traveled. To estimate emissions, these factors were\\ncombined with information about the activity levels of a\\nsource, such as the production levels at the facility, the number\\nof hours of operation, or the amount of fuel consumed.\\nBecause there are multiple programs investigating HAP\\nemissions in the United States, emissions data and source\\nactivity data are continually changing and improving. Since\\nestimating emissions requires making various assumptions, the\\nestimates are applicable for a specific time period and may not\\nnecessarily agree with other published estimates due to\\ndifferences in base years, emission factors and activity data,\\nand calculation assumptions. It should be recognized that\\nsome of the data presented in the NTI for a given base year is\\nlikely to change as more information and improved estimation\\napproaches are developed.\\nEPA established a hierarchy of emissions estimation\\nmethods in order to prepare the inventory. The hierarchy is\\nused to sort through overlapping data sources of varying\\nquality or reliability. EPA prefers to use existing inventories\\nthat are final, and whose estimates are judged to be acceptable.\\nThe hierarchy is (with data sources listed by preference):\\n1. Data developed by State and local air agencies;\\n2. Data from EPA\u00e2\u0080\u0099s Emissions Standards Division,\\ncollected and developed for standards development;\\n3. Data from existing EPA inventories, such as those\\ndeveloped to support requirements of CAA Sections\\n112(k) 4 and 112(c)(6); 5 and\\n4. Emissions reported in the TRI data base, 6 and\\nemissions that EPA generated using emission factors\\nand activity factors.\\nIf emissions data were not available for certain source\\ncategories through these references (1-4 above), emissions\\nfactors and activity data were used to estimate emissions.\\nEmission factors used were evaluated for their currency,\\ncompleteness, representativeness, and overall quality. The\\nemission factors generally came from EPA\u00e2\u0080\u0099s AP-42\\ndocument, 7 EPA\u00e2\u0080\u0099s Locating and Estimating Document Series, 8\\nor the Factor Information Retrieval (FIRE) system. 9 Most of\\nthe activity data were obtained from sources such as the\\nEnergy Information Administration (fuel consumption\\nreports), the Forest Service (fires and burned acreage), and\\nother EPA offices (waste disposal reports). Industry trade\\npublications, commercially published business directories, and\\njournals were also sources of activity data.\\nThe EPA\u00e2\u0080\u0099s Office of Transportation and Air Quality\\n(OTAQ) assisted in the development of the mobile source\\nemissions estimates. Mobile sources include \u00e2\u0080\u009con-road\u00e2\u0080\u009d\\nvehicles, such as cars, trucks, and motorcycles, as well as\\n\u00e2\u0080\u009cnonroad\u00e2\u0080\u009d vehicles and equipment, such as airplanes, boats,\\nor lawnmowers. For many of the HAPs emitted from mobile\\nsources, details on the emission estimation procedures are\\nprovided in the Section 112(k) inventory report. 3\\n7.5.2 What are the NTI Base Years?\\nThe Baseline NTI (1990 1993)\\nThe first iteration of the NTI, referred to as the Baseline\\nNTI, provides a composite of emissions estimates\\nintended to represent the 1990 to 1993 time frame. Much\\nof the baseline NTI data are for 1990, because a large\\nportion of the national emissions data in the NTI was\\ndeveloped under the Section 112(c)(6) and Section 112(k)\\nprograms which targeted a 1990 base year. The TRI data\\nand state and local data included for California, Houston,\\nand Phoenix are for a 1993 base year. Emissions for the\\nMACT source category portion of the NTI are annual\\nemissions ranging from 1990 to 1993, and represent\\nHazardous Air Pollutants 7-3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0125.jp2"}, "126": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nemissions from these sources before MACT standards\\nwere implemented. The estimates in the Baseline\\ninventory are aggregated to the county level and cover the\\n50 United States. The emissions summaries and graphics\\nprovided in this report are based exclusively on the\\nBaseline NTI.\\nThe 1996 NTI\\nEPA has recently completed the 1996 NTI. The 1996\\nversion differs significantly from the Baseline NTI.\\nUnlike the Baseline NTI which has emissions estimates\\nfrom all counties by source category and pollutant, the\\n1996 NTI contains facility- and location-specific\\ninformation making it suitable for input to computer air\\nquality models (computer models used to for dispersion\\ncalculations which predict resultant ambient air\\nconcentrations). Methods for mobile source emissions\\nestimates were significantly improved in the 1996 NTI\\nalso. The 1996 NTI data set contains estimates for all 50\\nUnited States and for Puerto Rico and the Virgin Islands.\\nIt has been compiled in cooperation with State and local\\nagencies which have submitted data they have gathered\\nduring facility permitting and other regulatory activities.\\nThe 1996 NTI contains data and/or comments supplied by\\n46 States, Puerto Rico, and the Virgin Islands. Figure 7-1\\nhighlights the state and local agencies that contributed\\ndata to the 1996 NTI. Subsequent base year NTIs will\\ncontain this same level of model-ready detail and will be\\ncompiled every 3 years (1999, 2002, etc.).\\nThe 1996 NTI was completed in January 2000, but the\\nresults could not be summarized for comparison to Baseline\\nNTI emissions in time to be printed in this document. Thus,\\nbecause only one data set is summarized here, this report does\\nnot show an emissions trend over time. Instead, it provides the\\nbaseline from which trends can be measured in future reports.\\n7.5.3 How are Emissions Allocated to Source\\nTypes and Counties?\\nFor purposes of the Baseline NTI, the emission estimates\\nwere further refined in two ways. First, the emissions were\\nallocated by source type including major sources, area sources\\nand mobile sources. Then the emissions were spatially\\nallocated. The sections below describe these analyses.\\nMajor/Area Source Allocation\\nThe national emission estimates for stationary source\\ncategories were allocated according to whether the emitting\\nsource category was classified as \u00e2\u0080\u009cmajor,\u00e2\u0080\u009d \u00e2\u0080\u009carea,\u00e2\u0080\u009d or could be\\nclassified partially as both. According to Title I,\\nSection 112(a) of the C AA, a \u00e2\u0080\u009cmajor source\u00e2\u0080\u009d is any stationary\\nsource (including all emission points and units located within\\na contiguous area and under common control) of air pollution\\nthat has the potential to emit, considering controls, 10 tons or\\nmore per year of any HAP or 25 tons or more per year of any\\ncombination of HAPs. An \u00e2\u0080\u009carea source\u00e2\u0080\u009d is any stationary\\nsource of HAPs that does not qualify as a major source. Major\\nsources may include co-located sources which can have\\ncomponents that emit less that 10 tons per year of an\\nindividual HAP or 25 tons or more per year of any\\ncombination of HAP.\\nSpatial Allocation\\nEmissions were assigned to counties by a number of\\nmethods. In some cases, where actual locations were not\\nknown, emissions were assigned to individual counties using\\nsurrogate approaches. Some examples of surrogate\\napproaches include proportioning national emissions to\\ncounties based on population, proportioning emissions from\\nsome industrial sectors to counties based on 1990 Standard\\nIndustrial Classification (SIC) code employment estimates,\\nand assigning emissions from forest fires to counties based on\\nforested acres.\\n7.5.4 What are Urban/Rural Allocations?\\nThe emission estimates were also spatially allocated on an\\nurban and rural basis in order to meet some of the\\nrequirements of the Integrated Urban Air Toxics Strategy. To\\ndo this, U.S. Census Bureau statistical data were used. 9 The\\nCensus Bureau has designated the portion of every county in\\nthe United States that is considered urban. The criteria used\\ninclude population density and total population. Using\\npopulation data and urban designations, every county in the\\nUnited States was classified as one of the following\\ncategories:\\nUrban-1 (U1) counties are included in a metropolitan\\nstatistical area with a population greater than\\n250,000;\\nUrban-2 (U2) counties in which the Census Bureau\\ndesignates more than 50 percent of the county\\npopulation as urban; and\\nRural (R) counties in which the Census Bureau\\ndesignates less than 50 percent of the county\\npopulation as urban.\\nIn the summary of 1993 NTI emissions and graphics that\\nfollow, \u00e2\u0080\u009curban\u00e2\u0080\u009d has been designated to be the sum of U1 plus\\nU2 counties. Figure 7-2 identifies the urban/rural counties in\\nthe 50 United States using the Integrated Urban Air Toxics\\nStrategy definition described above. Note that these urban/\\nrural designations have been derived exclusively for inventory\\npurposes and do not indicate regulatory applicability.\\n7-4 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0126.jp2"}, "127": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n7.5.5 What Changes Have Been Made Since\\nthe Last Trends Report?\\nEmission inventories are dynamic, with enhancements\\nbeing made on an ongoing basis. Many revisions were made\\nin the Baseline NTI since what was reported in the last Trends\\ndocument. Public review of the compilation of the Section\\n112(k) Urban Air Toxics inventory and new information that\\nbecame available through the MACT/GACT program led to\\nmost of these changes. Some errors in the earlier data base\\nwere also corrected. These changes led to a significant\\ndecrease in the estimates of emissions from stationary sources.\\n7.6 HOW ARE THE EMISSIONS\\nSUMMARIZED?\\nThe emissions summarized in the following pages\\nrepresents the most recent version of the Baseline NTI. (This\\nversion is the \u00e2\u0080\u009c9901\u00e2\u0080\u009d version of the inventory and, as stated\\npreviously, represents a composite of emissions estimates from\\nthe 1990 to 1993 time period.) Because of the volume of data,\\nmuch of the emissions information shown here involves the\\nsummary of emissions across pollutants. This cross-pollutant\\nsummary is done primarily for the sake of comparison to show\\nthe mass of all HAP emissions across source sectors (major,\\narea, mobile), tier groups (industry sectors), populations\\ncenters (urban and rural), and geographic regions (national and\\nstate).\\nAny evaluation of exposure or resultant risk posed by\\nthese emissions would depend on the presence, exposure,\\nand toxicity of individual pollutants, and cannot be\\nsurmised from the data provided here.\\nThe sum of Baseline NTI emissions from all sources and\\nfrom the 50 United States is 5.9 million tons. This version\\n(9901) of the NTI includes emission estimates for 169 of the\\n188 individual and group (e.g., metal compound groups)\\nHAPs. A list of the HAPs included is presented in Table 7-1.\\nApproximately 580,000 tons of HAP emissions that could not\\nbe speciated into individual chemical species. These\\n\u00e2\u0080\u009cunspeciated HAP\u00e2\u0080\u009d emissions come primarily from the\\nsynthetic organic chemicals industry MACT data. These\\nemissions are primarily volatile organic compounds. A small\\nsubset (approximately 64 tons) of these emissions are metals\\nand other particulate matter. It should be noted that this will\\nPb to the undercounting of individual HAP species from these\\nsources, for example, benzene emissions. The Baseline NTI\\nincludes estimates for approximately 960 source categories.\\n7.6.1 What Individual Pollutant Detail is\\nGiven?\\nAs part of the Integrated Urban Air Toxics Strategy, EPA\\nidentified a list of the 33 air toxics that present the greatest\\nthreat to public health in the largest number of urban areas (see\\nTable 7-2 for list of urban air toxics). In identifying the list of\\n\u00e2\u0080\u009curban air toxics\u00e2\u0080\u009d pollutants EPA looked at pollutants\\nregardless of the source sector (major, area, or mobile), from\\nwhich they were emitted. Thus, EPA looked at pollutants that\\npose a health threat in urban areas in the aggregate, from\\nstationary area, stationary major and mobile sources.\\nHowever, the CAA requires that EPA identify at least 30\\nHAPs that \u00e2\u0080\u009cresult from area sources.\u00e2\u0080\u009d Thus, of these 33 urban\\nair toxics, EPA identified the 30 with the greatest contribution\\nfrom smaller commercial and industrial operations or so-called\\n\u00e2\u0080\u009carea\u00e2\u0080\u009d sources. These 30 are important for establishing a list\\nof area source categories for regulation as required by section\\n112(k). However, in addition to the requirement to list area\\nsource categories, the Integrated Urban Air Toxics Strategy\\ncontains the three risk reduction goals discussed earlier. It is\\nimportant to remember that in looking at the risk reduction\\ngoals the Integrated Urban Air Toxics Strategy states EPA will\\nlook at the risk from all 188 HAPs, not just that associated\\nwith the 33 urban air toxics. The 33 urban air toxics represent\\nthose pollutants that are a priority on a national scale.\\nHowever, on the local scale other HAPs may be play a more\\nimportant role in local health risks. The emissions data that\\nfollows highlights the emissions of these 33 priority HAPs in\\ncomparison to all of the 188 HAPs. For additional background\\ninformation on the Integrated Urban Air Toxics Strategy, visit\\nEPA\u00e2\u0080\u0099s website at\\nhttp://www.epa.gov/ttn/uatw/urban/urbanpg.html.\\nAs explained previously, because the Integrated Urban\\nAir Toxics Strategy is designed to focus on emissions from\\nurban areas, all emissions in the NTI are flagged accordingly\\nto indicate whether the county from which the emissions come\\nmeets the urban definition. Figures 7-3 through Figure 7-5\\nindicate the percentages of national emissions totals that are\\nfrom rural and urban counties and attributable to the major,\\narea, on-road, and nonroad source sectors. Figures 7-6 and 7-7\\nshow the summed emissions of the 188 HAPs and 33 HAPs,\\nrespectively, by state and source sector. Figures 7-8 and 7-9\\npresent a map graphic portraying the percentiles of the\\nsummed emissions densities in tons per square mile. Figure\\n7-10 shows national emissions percentage of each of the 33\\nHAPs divided among source sectors (major, area, on-road,\\nnonroad).\\nThe Baseline NTI emissions are further summarized in\\nseveral ways. Table 7-3 includes all 188 HAPs summed by\\ntotal, urban, and rural allocations and by point, area, and\\nmobile (on-road and nonroad) contributions. Table 7-4 repeats\\nthis information with more detail about how the point, area,\\nand mobile sectors exist in urban and rural counties. Tables\\n7-5 and 7-6 indicate the summed 188 and 33 HAPs,\\nrespectively, by State and point, area, on-road, and nonroad\\nemissions. Tables 7-7 and 7-8 summarize the 33 HAPs by\\nsource tier groups. Tiering is a method of broadly categorizing\\nindustry sectors. Tier 1 provides the most general\\nclassification (e.g., fuel combustion) with Tier 2 supplying\\nmore detail (e.g., fuel combustion by coal, oil, gas, and other\\nHazardous Air Pollutants 7-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0127.jp2"}, "128": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nfuel types). Although currently criteria pollutant xind HAP\\nemission inventories are compiled separately, and therefore the\\nTier groups could not be matched exactly, every effort has\\nbeen made to match Tier groups as much as possible. Table 7-\\n7 indicates Tier 1 groups and Table 7-8, Tier 1 along with\\nTier 2.\\nWithin the Tier 2 groupings, emissions in the NTI are\\nflagged according to whether they come from source\\ncategories being reviewed for MACT/G ACT regulations. The\\nMACT source emissions that are flagged in the Baseline NTI\\ndata set reflect source categories for which EPA has developed\\nemissions estimates as part of ongoing regulatory develop\u00c2\u00ac\\nment. Although utility emissions have a \u00e2\u0080\u009cMACT flag,\u00e2\u0080\u009d no\\ndetermination has been made as yet regarding whether these\\nsources will be subject to MACT standards. Combustion\\nsources being reviewed under section 129 are also flagged.\\nThe source categories and pollutants that are MACT flagged\\nindicate those considered in the Integrated Urban Strategy\\nanalyses (used to determine the list of priority HAPs) prior to\\npublication of the Strategy. That analysis resulted in an\\nadditional listing of source categories, published in the\\nJuly 19, 1999 Federal Registerr These newly listed source\\ncategories do not yet have MACT flags in the NTI; once\\nstandards have been initiated to the point that emissions\\ncovered by new standards can be identified, the inventory will\\nreflect them.\\n7.7 REFERENCES\\n1. This list originally included 189 chemicals. The CAA allows EPA to modify this list if new scientific information\\nbecomes available that indicates a change should be made. Using this authority, the Agency modified the list to remove\\ncaprolactam in 1996, reducing the list to 188 pollutants (Hazardous Air Pollutant List; Modification, 61 FR 30816,\\nJune 18, 1996).\\n2. \u00e2\u0080\u009cNational Air Toxics Program: The Integrated Urban Strategy;\u00e2\u0080\u009d Notice, Federal Register 64:38705, U.S. Environmental\\nProtection Agency. July 19, 1999.\\n3. \u00e2\u0080\u009cEPA Strategic Plan,\u00e2\u0080\u009d EPA-190/R-97-002, Office of the Chief Financial Officer, U.S. Environmental Protection\\nAgency, U.S. Government Printing Office, Washington, DC. 1997.\\n4. \u00e2\u0080\u009c1990 Emissions Inventory of Forty Potential Section 112(k) Pollutants,\u00e2\u0080\u009d Supporting Data for EPA\u00e2\u0080\u0099s Section 112(k)\\nRegulatory Strategy, Final Report, Office of Air Quality Planning and Standards, U.S. Environmental Protection\\nAgency. Research Triangle Park, NC. 1999.\\n5. \u00e2\u0080\u009c1990 Emissions Inventory of Section 112(c)(6) Pollutants: Polycyclic Organic Matter (POM), 2,3,7,8-\\nTetrachlorodibenzo-P-Dioxin (TCDD)/2,3,7,8-Tetrachlorodibenzofuran (TCDF), Polychlorinated Biphenyl Compounds\\n(PCBs), Hexachlorobenzene, Mercury, and Alkylated Lead,\u00e2\u0080\u009d Office of Air Quality Planning and Standards, U.S.\\nEnvironmental Protection Agency, Research Triangle Park, NC. 1999.\\n6. \u00e2\u0080\u009cToxics Release Inventory 1987-1995 CD ROM,\u00e2\u0080\u009d EPA 749-C-96-003, U.S. Environmental Protection Agency, Research\\nTriangle Park, NC. 1996a.\\n7. \u00e2\u0080\u009cCompilation of Air Pollutant Emission Factors, Fifth Edition and Supplements,\u00e2\u0080\u009d AP-42, Volume I: Stationary Point and\\nArea Sources, U.S. Environmental Protection Agency, Research Triangle Park, NC. 1996.\\n8. \u00e2\u0080\u009cAir Chief Compact Disc,\u00e2\u0080\u009d Version 7, EPA 454/C-99-004, U.S. Environmental Protection Agency, Research Triangle\\nPark, NC. November 1999.\\n9. \u00e2\u0080\u009cFactor Information Retrieval (FIRE) System Database,\u00e2\u0080\u009d Version 5.1a, U.S. Environmental Protection Agency, Research\\nTriangle Park, NC. 1995.\\n10. \u00e2\u0080\u009c1990 Summary Tape File 1A, 1990 Decennial Census of Population and Housing,\u00e2\u0080\u009d U.S. Census Bureau, Washington,\\nDC. 1990.\\n7-6 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0128.jp2"}, "129": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\nTable 7-1. Hazardous Air Pollutants Included in the Baseline NTI (version 9901)\\n1,1,2,2-Tetrachloroethane\\n1.1.2- Trichloroethane\\n1,1 -Dimethylhydrazine\\n1.2.4- Trichlorobenzene\\n1.2- Dibromo-3-chloropropane\\n1.2- Epoxybutane\\n1.2- Propylenimine (2-Methylaziridine)\\n1.3- Butadiene\\n1.3- Dichloropropene\\n1.3- Propane sultone\\n1.4- Dichlorobenzene\\n1.4- Dioxane (1,4-Diethyleneoxide)\\n2.2.4- Trimethylpentane\\n2,3,7,8-TCDD TEQ\\n2.4.5- Trichlorophenol\\n2.4.6- Trichlorophenol\\n2.4- D (2,4-Dichlorophenoxyacetic Acid)(including salts\\nand esters)\\n2.4- Dinitrophenol\\n2.4- Dinitrotoluene\\n2.4- Toluene diisocyanate\\n2-Chloroacetophenone\\n2-Nitropropane\\n3,3 -Dichlorobenzidene\\n3,3 -Dimethoxybenzidine\\n3,3 -Dimethylbenzidine\\n4,4 -Methylenebis(2-chloroaniline)\\n4,4 -Methylenedianiline\\n4,4 -Methylenediphenyl diisocyanate (MDI)\\n4.6- Dinitro-o-cresol (including salts)\\n4-Aminobiphenyl\\n4-Dimethylaminoazobenzene\\n4-Nitrobiphenyl\\n4-Nitrophenol\\nAcetaldehyde\\nAcetamide\\nAcetonitrile\\nAcetophenone\\nAcrolein\\nAcrylamide\\nAcrylic acid\\nAcrylonitrile\\nAllyl chloride\\nAniline\\nAntimony Compounds\\nArsenic Compounds(inorganic including arsine)\\nAsbestos\\nBenzene (including benzene from gasoline)\\nBenzidine\\nBenzotrichloride\\nBenzyl chloride\\nBeryllium Compounds\\nBiphenyl\\nBis(2-ethylhexyl)phthalate (DEHP)\\nBis(chloromethyl) ether\\nBromoform\\nCadmium Compounds\\nCalcium cyanamide\\nCaptan\\nCarbaryl\\nCarbon disulfide\\nCarbon tetrachloride\\nCarbonyl sulfide\\nCatechol\\nChlordane\\nChlorine\\nChloroacetic acid\\nChlorobenzene\\nChlorobenzilate\\nChloroform\\nChloromethyl methyl ether\\nChloroprene\\nChromium Compounds\\nCobalt Compounds\\nCoke Oven Emissions\\nCresol/Cresylic acid (mixed isomers)\\nCumene\\nHazardous Air Pollutants 7-7", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0129.jp2"}, "130": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 7-1 (continued)\\nCyanide Compounds\\nDibutyl phthalate\\nDichloroethyl ether (Bis[2-chloroethyl]ether)\\nDichlorvos\\nDiethanolamine\\nDiethyl sulfate\\nDimethyl phthalate\\nDimethyl sulfate\\nEpichlorohydrin (l-Chloro-2,3-epoxypropane)\\nEthyl Chloride\\nEthyl acrylate\\nEthyl carbamate (Urethane) chloride (Chloroethane)\\nEthylbenzene\\nEthylene dibromide (Dibromoethane)\\nEthylene dichloride (1,2-Dichloroethane)\\nEthylene glycol\\nEthylene oxide\\nEthylene thiourea\\nEthylidene dichloride (1,1 -Dichloroethane)\\nFine mineral fibers\\nFormaldehyde\\nGlycol ethers\\nHeptachlor\\nHexachlorobenzene\\nHexachlorobutadiene\\nHexachlorocyclopentadiene\\nHexachloroethane\\nHexamethylene diisocyanate\\nHexane\\nHydrazine\\nHydrochloric acid (Hydrogen chloride [gas only])\\nHydrogen fluoride (Hydrofluoric acid)\\nHydroquinone\\nIsophorone\\nLead Compounds\\nMaleic anhydride\\nManganese Compounds\\nMercury Compounds\\nMethoxychlor\\nMethyl bromide (Bromomethane)\\nMethyl chloride (Chloromethane)\\nMethyl chloroform (1,1,1 -Trichloroethane)\\nMethyl ethyl ketone (2-Butanone)\\nMethyl iodide (lodomethane)\\nMethyl isobutyl ketone (Hexone)\\nMethyl isocyanate\\nMethyl methacrylate\\nMethyl tert-butyl ether\\nMethylene chloride (Dichloromethane)\\nMethylhydrazine\\nN,N-Dimethylaniline\\nN,N-Dimethylformamide\\nN-Nitrosodimethylamine\\nN-Nitrosomorpholine\\nNickel Compounds\\nNitrobenzene\\nParathion\\nPentachloronitrobenzene (Quintobenzene)\\nPentachlorophenol\\nPhenol\\nPhosgene\\nPhosphine\\nPhosphorus Compounds\\nPhthalic anhydride\\nPolychlorinated biphenyls (Aroclors)\\nPolycyclic Organic Matter\\nPropionaldehyde\\nPropoxur (Baygon)\\nPropylene dichloride (1,2-Dichloropropane)\\nPropylene oxide\\nQuinoline\\nQuinone (p-Benzoquinone)\\nRadionuclides (including radon)\\nSelenium Compounds\\nStyrene\\nStyrene oxide\\n7-8 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0130.jp2"}, "131": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 7-1 (continued)\\nMethanol\\nTetrachloroethylene (Perchloroethylene)\\nTitanium tetrachloride\\nVinyl acetate\\nToluene\\nVinyl bromide\\nTotal Unspeciated HAPS\\nVinyl chloride\\nTotal Unspeciated METALS\\nVinylidene chloride (1,1-Dichloroethylene)\\nTrichloroethylene\\nXylenes (mixed isomers)\\nTriethylamine\\no-Anisidine\\nTrifluralin\\no-Toluidine\\nUnspeciated Particulate HAPs, Chromium and Cobalt\\np-Phenylenediamine\\nHazardous Air Pollutants 7-9", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0131.jp2"}, "132": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 7-2. List of Urban HAPS for the Integrated Urban Air Toxics Strategy\\n(\u00e2\u0080\u009cUrban HAPS List\u00e2\u0080\u009d)\\nHAP\\nCAS No.\\nHAP\\nCAS No.\\nacetaldehyde\\n75070\\nformaldehyde\\n50000\\nacrolein\\n107028\\nhexachlorobenzene\\n118741\\nacrylonitrile\\n107131\\nhydrazine\\n302012\\narsenic compounds\\nlead compounds\\nbenzene\\n71432\\nmanganese compounds\\nberyllium compounds\\nmercury compounds\\n1,3-butadiene\\n106990\\nmethylene chloride (dichloromethane)\\n75092\\ncadmium compounds\\nnickel compounds\\ncarbon tetrachloride\\n56235\\npolychlorinated biphenyls (PCBs)\\n1336363\\nchloroform\\n67663\\npolycyclic organic matter (POM)\\nchromium compounds\\nquinoline\\n91225\\ncoke oven emissions\\n8007452\\n2,3,7,8-tetrachlorodibenzo-p-dioxin\\ncongeners TCDF congeners)\\n1746016\\n1,2-dibromoethane\\n106934\\n1,1,2,2-tetrachloroethane\\n79345\\n1,2-dichloropropane (propylene dichloride)\\n78875\\ntetrachloroethylene (perchloroethylene)\\n127F84\\n1,3-dichloropropene\\n542756\\ntrichloroethylene\\n79016\\nethylene dichloride\\n(1,2-dichloroethane)\\n107062\\nvinyl chloride\\n75014\\nethylene oxide\\n75218\\nChemical Abstracts System number.\\n7-10 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0132.jp2"}, "133": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\nTable 7-3. Baseline NTI Emissions for Urban, Rural, and\\nMajor Source Categories by HAP\\n188 HAP Name\\nTotal National\\nEmissions\\n(tpy)\\nTotal URBAN\\nTotal RURAL\\nTotal Point\\nTotal Area\\nMobile:\\nOnroad\\nMobile:\\nNonroad\\n1,1,2,2-Tetrachloroethane\\n248.56834\\n209.64691\\n38.92143\\n50.21984\\n198.34850\\n0.00000\\n0.00000\\n1,1,2-Trichloroethane\\n761.36164\\n511.34897\\n250.01267\\n754.41778\\n6.94386\\n0.00000\\n0.00000\\n1,1 -Dimethylhydrazine\\n0.58484\\n0.57639\\n0.00845\\n0.58313\\n0.00170\\n0.00000\\n0.00000\\n1,2,4-Trichlorobenzene\\n5,865.94500\\n3,072.21190\\n2,793.73310\\n5,849.83966\\n16.10534\\n0.00000\\n0.00000\\n1,2-Dibromo-3-chloropropane\\n14.93700\\n11.17880\\n3.75820\\n14.78763\\n0.14937\\n0.00000\\n0.00000\\n1,2-Epoxybutane\\n38.05489\\n37.15589\\n0.89900\\n36.61370\\n1.44120\\n0.00000\\n0.00000\\n1,2-Propylenimine (2-Methylaziridine)\\n0.41950\\n0.40444\\n0.01506\\n0.41043\\n0.00907\\n0.00000\\n0.00000\\n1,3-Butadiene\\n71,523.56768\\n42,590.06162\\n28,933.50606\\n3,937.92968\\n20,040.53479\\n36,657.97824\\n10,887.12496\\n1,3-Dichloropropene\\n19,927.87000\\n16,652.12824\\n3,275.74176\\n30.48629\\n19,897.38371\\n0.00000\\n0.00000\\n1,3-Propane sultone\\n0.00072\\n0.00072\\n0.00000\\n0.00072\\n0.00000\\n0.00000\\n0.00000\\n1,4-Dichlorobenzene\\n5,225.64801\\n4,228.57842\\n997.06959\\n750.16231\\n4,475.48569\\n0.00000\\n0.00000\\n1,4-Dioxane (1,4-Diethyleneoxide)\\n855.24718\\n716.54579\\n138.70139\\n832.48441\\n22.76276\\n0.00000\\n0.00000\\n2,2,4-Trimethylpentane\\n29,627.36202\\n25,490.36625\\n4,136.99577\\n23,821.53979\\n5,803.52238\\n1.81653\\n0.48333\\n2,3,7,8-TCDDTEQ\\n0.00264\\n0.00221\\n0.00043\\n0.00170\\n0.00084\\n0.00009\\n0.00000\\n2,4,5-Trichlorophenol\\n0.52300\\n0.39141\\n0.13159\\n0.51777\\n0.00523\\n0.00000\\n0.00000\\n2,4,6-Trichlorophenol\\n0.59785\\n0.46601\\n0.13184\\n0.59017\\n0.00768\\n0.00000\\n0.00000\\n2,4-D (2,4-Dichlorophenoxyacetic\\nAcid)(including salts and esters)\\n7,681.23909\\n2,503.84525\\n5,177.39385\\n0.64196\\n7,680.59714\\n0.00000\\n0.00000\\n2,4-Dinitrophenol\\n7.74550\\n7.08346\\n0.66204\\n7.72507\\n0.02044\\n0.00000\\n0.00000\\n2,4-Dinitrotoluene\\n3.50850\\n2.88957\\n0.61893\\n0.59401\\n2.91450\\n0.00000\\n0.00000\\n2,4-Toluene diisocyanate\\n67.40469\\n54.59477\\n12.80992\\n64.68525\\n2.71945\\n0.00000\\n0.00000\\n2-Chloroacetophenone\\n0.02800\\n0.02096\\n0.00704\\n0.02772\\n0.00028\\n0.00000\\n0.00000\\n2-Nitropropane\\n55.46246\\n52.15140\\n3.31106\\n54.21458\\n1.24787\\n0.00000\\n0.00000\\n3,3 -Dichlorobenzidene\\n0.51705\\n0.38807\\n0.12897\\n0.51189\\n0.00515\\n0.00000\\n0.00000\\n3,3 -Dimethoxybenzidine\\n0.87700\\n0.65634\\n0.22066\\n0.86823\\n0.00877\\n0.00000\\n0.00000\\n3,3 -Dimethylbenzidine\\n0.31600\\n0.23649\\n0.07951\\n0.31284\\n0.00316\\n0.00000\\n0.00000\\n4,4 -Methylenebis(2-chloroaniline)\\n0.92945\\n0.61097\\n0.31848\\n0.91624\\n0.01321\\n0.00000\\n0.00000\\n4,4 -Methylenedianiline\\n3.97348\\n3.61660\\n0.35689\\n3.83849\\n0.13500\\n0.00000\\n0.00000\\n4,4 -Methylenediphenyl diisocyanate (MDI)\\n244.24576\\n117.53081\\n126.71495\\n195.79506\\n48.45070\\n0.00000\\n0.00000\\n4,6-Dinitro-o-cresol (including salts)\\n0.58850\\n0.44471\\n0.14379\\n0.58262\\n0.00588\\n0.00000\\n0.00000\\n4-Aminobiphenyl\\n0.18200\\n0.13621\\n0.04579\\n0.18018\\n0.00182\\n0.00000\\n0.00000\\n4-Dimethylaminoazobenzene\\n0.30800\\n0.23051\\n0.07749\\n0.30492\\n0.00308\\n0.00000\\n0.00000\\n4-Nitrobiphenyl\\n0.37300\\n0.27915\\n0.09385\\n0.36927\\n0.00373\\n0.00000\\n0.00000\\n4-Nitrophenol\\n1.54100\\n1.17946\\n0.36154\\n1.52561\\n0.01539\\n0.00000\\n0.00000\\nAcetaldehyde\\n137,166.15337\\n78,064.33352\\n59,101.81986\\n21,337.93570\\n50,533.50105\\n27,963.87210\\n37,330.84452\\nAcetamide\\n0.02806\\n0.02425\\n0.00381\\n0.01080\\n0.01726\\n0.00000\\n0.00000\\nAcetonitrile\\n1,450.60505\\n1,241.98190\\n208.62315\\n1,393.62584\\n56.97922\\n0.00000\\n0.00000\\nAcetophenone\\n291.09852\\n229.79161\\n61.30691\\n284.07511\\n7.02341\\n0.00000\\n0.00000\\nAcrolein\\n62,660.26492\\n28,916.89707\\n33,743.36785\\n757.25478\\n49,632.35798\\n5,541.61622\\n6,729.03594\\nAcrylamide\\n35.44595\\n33.50764\\n1.93831\\n34.59024\\n0.85571\\n0.00000\\n0.00000\\nAcrylic acid\\n537.18231\\n497.56824\\n39.61407\\n523.19176\\n13.99055\\n0.00000\\n0.00000\\nAcrylonitrile\\n2,543.60095\\n2,240.67795\\n302.92301\\n2,072.52780\\n471.07315\\n0.00000\\n0.00000\\nAllyl chloride\\n111.88139\\n100.70670\\n11.17469\\n109.10577\\n2.77563\\n0.00000\\n0.00000\\nAniline\\n477.45592\\n397.74288\\n79.71305\\n463.54493\\n13.91100\\n0.00000\\n0.00000\\nAntimony Compounds\\n103.37891\\n79.04959\\n24.32932\\n96.76993\\n6.60794\\n0.00092\\n0.00012\\nArsenic Compounds(inorganic including arsine)\\n288.43199\\n203.83865\\n84.59334\\n230.28133\\n55.36306\\n1.74759\\n1.04001\\nAsbestos\\n8.50164\\n6.49092\\n2.01072\\n7.22413\\n1.27752\\n0.00000\\n0.00000\\nBenzene (including benzene from gasoline)\\n389,347.91615\\n258,044.08078\\n131,303.83537\\n36,440.67051\\n73,236.15328\\n207,259.79811\\n72,411.29424\\nBenzidine\\n0.40000\\n0.30137\\n0.09863\\n0.39578\\n0.00422\\n0.00000\\n0.00000\\nBenzotrichloride\\n10.23650\\n7.92716\\n2.30934\\n10.02818\\n0.20832\\n0.00000\\n0.00000\\nBenzyl chloride\\n33.55681\\n28.15413\\n5.40268\\n31.98701\\n1.56979\\n0.00000\\n0.00000\\nHazardous Air Pollutants 7-11", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0133.jp2"}, "134": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\nTable 7-3 (continued)\\n188 HAP Name\\nTotal National\\nEmissions\\n(tpy)\\nTotal URBAN\\nTotal RURAL\\nTotal Point\\nTotal Area\\nMobile:\\nOnroad\\nMobile:\\nNonroad\\nBeryllium Compounds\\n12.39344\\n8.52101\\n3.87243\\n9.75393\\n2.61950\\n0.00000\\n0.02000\\nBiphenyl\\n863.26496\\n557.22057\\n306.04439\\n832.45108\\n30.79378\\n0.01470\\n0.00539\\nBis(2-ethylhexyl)phthalate (DEHP)\\n859.69315\\n634.86878\\n224.82437\\n814.37464\\n45.31851\\n0.00000\\n0.00000\\nBis(chloromethyl) ether\\n0.43589\\n0.40250\\n0.03339\\n0.42541\\n0.01048\\n0.00000\\n0.00000\\nBromoform\\n8.47200\\n6.34042\\n2.13158\\n8.38728\\n0.08472\\n0.00000\\n0.00000\\nCadmium Compounds\\n199.12086\\n161.96437\\n37.15649\\n158.93650\\n39.87356\\n0.00068\\n0.31011\\nCalcium cyanamide\\n6.31000\\n6.31000\\n0.00000\\n3.55821\\n2.75179\\n0.00000\\n0.00000\\nCaptan\\n2.16500\\n1.88151\\n0.28349\\n2.14356\\n0.02144\\n0.00000\\n0.00000\\nCarbaryl\\n1.91825\\n0.80109\\n1.11716\\n0.01337\\n1.90489\\n0.00000\\n0.00000\\nCarbon disulfide\\n130,279.58604\\n73,572.05191\\n56,707.53414\\n129,372.03640\\n907.54965\\n0.00000\\n0.00000\\nCarbon tetrachloride\\n5,040.51156\\n2,948.70650\\n2,091.80506\\n4,941.43259\\n99.07897\\n0.00000\\n0.00000\\nCarbonyl sulfide\\n12,244.95793\\n10,303.97508\\n1,940.98285\\n10,028.32515\\n2,216.63278\\n0.00000\\n0.00000\\nCatechol\\n12.72200\\n12.72108\\n0.00092\\n10.39509\\n2.32692\\n0.00000\\n0.00000\\nChlordane\\n0.05100\\n0.04766\\n0.00334\\n0.04894\\n0.00206\\n0.00000\\n0.00000\\nChlorine\\n77,392.29466\\n71,653.78964\\n5,738.50501\\n74,484.06927\\n2,908.11374\\n0.08699\\n0.02465\\nChloroacetic acid\\n40.85950\\n31.16850\\n9.69100\\n39.51657\\n1.34293\\n0.00000\\n0.00000\\nChlorobenzene\\n11,900.28694\\n8,919.49726\\n2,980.78968\\n2,827.48748\\n9,072.79946\\n0.00000\\n0.00000\\nChlorobenzilate\\n2.01430\\n2.01430\\n0.00000\\n2.01430\\n0.00000\\n0.00000\\n0.00000\\nChloroform\\n22,735.28325\\n13,243.25231\\n9,492.03094\\n22,158.72255\\n576.56070\\n0.00000\\n0.00000\\nChloromethyl methyl ether\\n6.18450\\n5.73760\\n0.44690\\n6.02049\\n0.16401\\n0.00000\\n0.00000\\nChloroprene\\n1,050.82941\\n1,014.07621\\n36.75320\\n1,039.40976\\n11.41966\\n0.00000\\n0.00000\\nChromium Compounds\\n897.15022\\n727.40183\\n169.74840\\n573.79284\\n269.62666\\n27.93068\\n25.80005\\nCobalt Compounds\\n65.69997\\n50.39620\\n15.30377\\n60.20699\\n5.49278\\n0.00017\\n0.00003\\nCoke Oven Emissions\\n1,763.69000\\n1,702.87310\\n60.81690\\n1,763.69000\\n0.00000\\n0.00000\\n0.00000\\nCresol/Cresylic acid (mixed isomers)\\n11,327.03156\\n6,194.55986\\n5,132.47171\\n11,316.14891\\n10.88266\\n0.00000\\n0.00000\\nCumene\\n11,418.27801\\n7,232.35156\\n4,185.92645\\n11,260.55879\\n157.71921\\n0.00000\\n0.00000\\nCyanide Compounds\\n2,405.32835\\n2,279.03686\\n126.29149\\n1,318.00259\\n1,087.32577\\n0.00000\\n0.00000\\nDibutyl phthalate\\n132.83833\\n109.90941\\n22.92892\\n126.25370\\n6.58464\\n0.00000\\n0.00000\\nDichloroethyl ether (Bis[2-chloroethyl]ether)\\n7.05000\\n3.68018\\n3.36982\\n6.20388\\n0.84612\\n0.00000\\n0.00000\\nDichlorvos\\n0.25750\\n0.11363\\n0.14387\\n0.25334\\n0.00417\\n0.00000\\n0.00000\\nDiethanolamine\\n86.25437\\n78.38355\\n7.87081\\n85.24043\\n1.01393\\n0.00000\\n0.00000\\nDiethyl sulfate\\n3.11950\\n2.79060\\n0.32890\\n3.04919\\n0.07031\\n0.00000\\n0.00000\\nDimethyl phthalate\\n153.74479\\n29.25621\\n124.48857\\n147.67810\\n6.06669\\n0.00000\\n0.00000\\nDimethyl sulfate\\n3.84856\\n2.23144\\n1.61712\\n3.31418\\n0.53437\\n0.00000\\n0.00000\\nEpichlorohydrin (l-Chloro-2,3-epoxypropane)\\n339.73705\\n301.08182\\n38.65523\\n328.80845\\n10.92860\\n0.00000\\n0.00000\\nEthyl Chloride\\n2,187.89548\\n1,724.48321\\n463.41227\\n2,023.60286\\n164.29262\\n0.00000\\n0.00000\\nEthyl acrylate\\n159.97414\\n151.47688\\n8.49726\\n153.58316\\n6.39099\\n0.00000\\n0.00000\\nEthyl carbamate (Urethane) chloride\\n(Chloroethane)\\n9.05249\\n7.73941\\n1.31309\\n8.49508\\n0.55742\\n0.00000\\n0.00000\\nEthylbenzene\\n150,602.95817\\n108,128.60788\\n42,474.35029\\n15,993.92246\\n3,698.17652\\n93,074.62992\\n37,836.22926\\nEthylene dibromide (Dibromoethane)\\n57.53988\\n37.63972\\n19.90017\\n53.93372\\n3.60617\\n0.00000\\n0.00000\\nEthylene dichloride (1,2-Dichloroethane)\\n4,198.60429\\n3,018.35098\\n1,180.25331\\n4,095.94988\\n102.65441\\n0.00000\\n0.00000\\nEthylene glycol\\n12,310.94365\\n9,807.54261\\n2,503.40104\\n11,396.21899\\n914.72465\\n0.00000\\n0.00000\\nEthylene oxide\\n2,761.74987\\n2,340.11324\\n421.63663\\n1,423.16536\\n1,338.58451\\n0.00000\\n0.00000\\nEthylene thiourea\\n1.68367\\n1.68367\\n0.00000\\n1.68367\\n0.00000\\n0.00000\\n0.00000\\nEthylidene dichloride (1,1-Dichloroethane)\\n273.34234\\n227.28584\\n46.05650\\n33.16484\\n240.17751\\n0.00000\\n0.00000\\nFine mineral fibers\\n0.44862\\n0.44862\\n0.00000\\n0.44862\\n0.00000\\n0.00000\\n0.00000\\nFormaldehyde\\n347,326.51381\\n199,513.35769\\n147,813.15612\\n30,493.37702\\n140,611.16651\\n96,816.50995\\n79,405.46035\\nGlycol ethers\\n68,264.06943\\n57,179.63996\\n11,084.42947\\n56,932.15300\\n11,331.91643\\n0.00000\\n0.00000\\nHeptachlor\\n0.03100\\n0.02897\\n0.00203\\n0.02975\\n0.00125\\n0.00000\\n0.00000\\nHexachlorobenzene\\n1.58467\\n1.29928\\n0.28539\\n1.01845\\n0.56622\\n0.00000\\n0.00000\\nHexachlorobutadiene\\n15.09100\\n11.08324\\n4.00776\\n14.89069\\n0.20031\\n0.00000\\n0.00000\\n7-12 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0134.jp2"}, "135": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 7-3 (continued)\\n188 HAP Name\\nTotal National\\nEmissions\\n(tpy)\\nTotal URBAN\\nTotal RURAL\\nTotal Point\\nTotal Area\\nMobile:\\nOnroad\\nMobile:\\nNonroad\\nHexachlorocyclopentadiene\\n4.07400\\n3.32985\\n0.74415\\n3.85667\\n0.21734\\n0.00000\\n0.00000\\nHexachloroethane\\n25.54000\\n24.54020\\n0.99980\\n6.19737\\n19.34263\\n0.00000\\n0.00000\\nHexamethylene diisocyanate\\n0.13974\\n0.13974\\n0.00000\\n0.13974\\n0.00000\\n0.00000\\n0.00000\\nHexane\\n188,727.94715\\n142,971.89168\\n45,756.05548\\n60,034.41637\\n23,237.08544\\n80,624.60109\\n24,831.84425\\nHydrazine\\n20.46295\\n13.27919\\n7.18377\\n19.06044\\n1.40251\\n0.00000\\n0.00000\\nHydrochloric acid (Hydrogen chloride [gas only])\\n339,677.12607\\n249,698.74905\\n89,978.37702\\n298,750.97695\\n40,926.14911\\n0.00000\\n0.00000\\nHydrogen fluoride (Hydrofluoric acid)\\n33,883.94892\\n21,979.39136\\n11,904.55757\\n31,841.65853\\n2,042.29040\\n0.00000\\n0.00000\\nHydroquinone\\n90.38896\\n68.97085\\n21.41811\\n89.44520\\n0.94376\\n0.00000\\n0.00000\\nIsophorone\\n402.62448\\n290.36651\\n112.25797\\n281.70725\\n120.91723\\n0.00000\\n0.00000\\nLead Compounds\\n3,307.14259\\n2,738.84886\\n568.29373\\n1,690.88478\\n419.99999\\n418.01335\\n778.24448\\nMaleic anhydride\\n215.24860\\n191.48367\\n23.76493\\n212.31816\\n2.93044\\n0.00000\\n0.00000\\nManganese Compounds\\n2,908.92074\\n2,007.63778\\n901.28296\\n2,349.91056\\n506.98243\\n21.68763\\n30.34011\\nMercury Compounds\\n205.95234\\n163.65582\\n42.29652\\n123.36402\\n70.69372\\n4.96458\\n6.93002\\nMethanol\\n385,706.55818\\n253,285.37433\\n132,421.18385\\n294,128.87245\\n91,577.65111\\n0.00000\\n0.03462\\nMethoxychlor\\n0.04800\\n0.04800\\n0.00000\\n0.04648\\n0.00152\\n0.00000\\n0.00000\\nMethyl bromide (Bromomethane)\\n30,984.83370\\n24,978.61034\\n6,006.22336\\n3,144.75726\\n27,840.07644\\n0.00000\\n0.00000\\nMethyl chloride (Chloromethane)\\n6,448.11666\\n5,420.61004\\n1,027.50662\\n6,278.24335\\n169.87331\\n0.00000\\n0.00000\\nMethyl chloroform (1,1,1-Trichloroethane)\\n214,949.10156\\n185,432.31956\\n29,516.78200\\n137,397.75765\\n77,551.34391\\n0.00000\\n0.00000\\nMethyl ethyl ketone (2-Butanone)\\n207,791.18347\\n183,446.29278\\n24,344.89069\\n188,650.74773\\n19,140.23388\\n0.18848\\n0.01338\\nMethyl iodide (lodomethane)\\n36.85000\\n33.98526\\n2.86474\\n35.83947\\n1.01053\\n0.00000\\n0.00000\\nMethyl isobutyl ketone (Hexone)\\n35,693.57825\\n29,212.34520\\n6,481.23304\\n31,062.51426\\n4,631.06400\\n0.00000\\n0.00000\\nMethyl isocyanate\\n5.48950\\n4.93401\\n0.55549\\n5.31432\\n0.17517\\n0.00000\\n0.00000\\nMethyl methacrylate\\n1,844.52803\\n1,502.97025\\n341.55778\\n1,662.50712\\n182.02091\\n0.00000\\n0.00000\\nMethyl tert-butyl ether\\n14,433.46646\\n10,632.91143\\n3,800.55502\\n5,258.32154\\n9,175.14492\\n0.00000\\n0.00000\\nMethylene chloride (Dichloromethane)\\n124,285.50179\\n100,615.53602\\n23,669.96577\\n87,900.64802\\n36,384.85376\\n0.00000\\n0.00000\\nMethylhydrazine\\n0.01300\\n0.01136\\n0.00164\\n0.01284\\n0.00016\\n0.00000\\n0.00000\\nN,N-Dimethylaniline\\n22.57050\\n18.95418\\n3.61632\\n3.08854\\n19.48195\\n0.00000\\n0.00000\\nN,N-Dimethylformamide\\n3,284.93673\\n3,063.75202\\n221.18470\\n3,175.27412\\n109.66261\\n0.00000\\n0.00000\\nN-Nitrosodimethylamine\\n19.86900\\n18.39534\\n1.47367\\n19.28712\\n0.58189\\n0.00000\\n0.00000\\nN-Nitrosomorpholine\\n0.63000\\n0.47149\\n0.15851\\n0.62370\\n0.00630\\n0.00000\\n0.00000\\nNickel Compounds\\n1,329.52989\\n1,195.97140\\n133.55850\\n916.23402\\n318.41674\\n15.54908\\n79.33005\\nNitrobenzene\\n48.57008\\n44.84957\\n3.72051\\n47.33858\\n1.23150\\n0.00000\\n0.00000\\nParathion\\n0.61000\\n0.60750\\n0.00250\\n0.59066\\n0.01934\\n0.00000\\n0.00000\\nPentachloronitrobenzene (Quintobenzene)\\n2.45669\\n1.73269\\n0.72400\\n2.40955\\n0.04715\\n0.00000\\n0.00000\\nPentachlorophenol\\n6.20350\\n2.57703\\n3.62647\\n2.69357\\n3.50993\\n0.00000\\n0.00000\\nPhenol\\n11,514.93212\\n7,935.49774\\n3,579.43438\\n11,165.60703\\n349.32157\\n0.00000\\n0.00352\\nPhosgene\\n4.57351\\n3.91680\\n0.65671\\n4.43914\\n0.13437\\n0.00000\\n0.00000\\nPhosphine\\n3.13436\\n3.13436\\n0.00000\\n2.85807\\n0.27629\\n0.00000\\n0.00000\\nPhosphorus Compounds\\n161.98552\\n146.90031\\n15.08522\\n124.97520\\n37.01033\\n0.00000\\n0.00000\\nPhthalic anhydride\\n468.36056\\n425.68662\\n42.67394\\n437.88687\\n30.47368\\n0.00000\\n0.00000\\nPolychlorinated biphenyls (Aroclor6)\\n0.04958\\n0.03845\\n0.01114\\n0.02430\\n0.02528\\n0.00000\\n0.00000\\nPolycyclic Organic Matter\\n17,535.29518\\n13,232.81263\\n4,302.48255\\n7,585.71388\\n9,839.12904\\n76.98431\\n33.46794\\nPropionaldehyde\\n14,187.80399\\n10,363.07906\\n3,824.72492\\n2,461.84192\\n6.07369\\n5,283.05624\\n6,436.83213\\nPropoxur (Baygon)\\n0.00500\\n0.00500\\n0.00000\\n0.00478\\n0.00022\\n0.00000\\n0.00000\\nPropylene dichloride (1,2-Dichloropropane)\\n654.98931\\n541.79724\\n113.19208\\n611.35524\\n43.63406\\n0.00000\\n0.00000\\nPropylene oxide\\n3,257.81786\\n2,939.97556\\n317.84229\\n2,923.70035\\n334.11751\\n0.00000\\n0.00000\\nQuinoline\\n26.02550\\n24.02860\\n1.99690\\n25.52454\\n0.50096\\n0.00000\\n0.00000\\nQuinone (p-Benzoquinone)\\n8.05050\\n6.99636\\n1.05414\\n7.97080\\n0.07970\\n0.00000\\n0.00000\\nRadionuclides (including radon)\\n7.80214\\n7.72292\\n0.07922\\n7.80214\\n0.00000\\n0.00000\\n0.00000\\nSelenium Compounds\\n355.37407\\n257.83442\\n97.53965\\n335.16779\\n19.66621\\n0.00006\\n0.54001\\nStyrene\\n56,139.36148\\n41,332.13409\\n14,807.22739\\n32,326.89290\\n3,811.43977\\n17,777.70916\\n2,223.31966\\nStyrene oxide\\n0.17600\\n0.17548\\n0.00052\\n0.17242\\n0.00359\\n0.00000\\n0.00000\\nHazardous Air Pollutants 7-13", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0135.jp2"}, "136": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 7-3 (continued)\\n188 HAP Name\\nTotal National\\nEmissions\\n(tpy)\\nTotal URBAN\\nTotal RURAL\\nTotal Point\\nTotal Area\\nMobile:\\nOnroad\\nMobile:\\nNonroad\\nTetrachloroethylene (Perchloroethylene)\\n128,000.71200\\n105,308.90354\\n22,691.80846\\n22,960.63954\\n105,040.07247\\n0.00000\\n0.00000\\nTitanium tetrachloride\\n6.24600\\n5.71788\\n0.52812\\n6.12960\\n0.11640\\n0.00000\\n0.00000\\nToluene\\n1,108,201.65839\\n792,801.42530\\n315,400.23308\\n195,867.77842\\n129,771.36341\\n631,796.16151\\n150,766.35504\\nTotal Unspeciated HAPs\\n580,281.00000\\n508,817.13009\\n71,463.86991\\n575,265.21000\\n5,015.79000\\n0.00000\\n0.00000\\nTotal Unspeciated METALS\\n64.31000\\n54.17513\\n10.13487\\n63.66690\\n0.64310\\n0.00000\\n0.00000\\nTrichloroethylene\\n71,998.64943\\n63,351.74653\\n8,646.90290\\n58,240.01715\\n13,758.63228\\n0.00000\\n0.00000\\nTriethylamine\\n443.52550\\n403.50053\\n40.02497\\n328.89055\\n114.63494\\n0.00000\\n0.00000\\nTrifluralin\\n10.15027\\n9.08566\\n1.06461\\n9.82151\\n0.32876\\n0.00000\\n0.00000\\nUnspeciated Particulate HAPs, Chromium and\\nCobalt\\n0.43000\\n0.37840\\n0.05160\\n0.31820\\n0.11180\\n0.00000\\n0.00000\\nVinyl acetate\\n3,864.49624\\n3,281.14888\\n583.34736\\n3,730.06177\\n134.43448\\n0.00000\\n0.00000\\nVinyl bromide\\n1.43700\\n1.32001\\n0.11699\\n1.42743\\n0.00958\\n0.00000\\n0.00000\\nVinyl chloride\\n2,712.08592\\n2,389.81085\\n322.27507\\n2,142.66959\\n569.41633\\n0.00000\\n0.00000\\nVinylidene chloride (1,1-Dichloroethylene)\\n223.89224\\n208.88484\\n15.00740\\n176.57818\\n47.31406\\n0.00000\\n0.00000\\nXylenes (mixed isomers)\\n702,577.76064\\n509,581.85529\\n192,995.90535\\n130,837.39623\\n65,901.91643\\n355,204.93935\\n150,633.50864\\no-Anisidine\\n0.82360\\n0.67164\\n0.15196\\n0.81440\\n0.00921\\n0.00000\\n0.00000\\no-Toluidine\\n9.30050\\n8.73017\\n0.57033\\n8.72284\\n0.57765\\n0.00000\\n0.00000\\np-Phenylenediamine\\n2.13950\\n1.84372\\n0.29578\\n2.11602\\n0.02348\\n0.00000\\n0.00000\\nNote(s): The estimates included in these tables have uncertainties and will improve/change as better data and estimation techniques become available over time.\\n7-14 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0136.jp2"}, "137": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nS .E\\no o\\ny- Q_\\no tT\\n*1 o\\no\\nO) o\\ncn Q)\\nT-^C/)\\nnr 0\\nt- o\\n0 O\\n.E 0\\n0 o\\nS g\\n(0 0\\nGO c\\n.2\\n4\\n0\\np- c\\n0 U)\\n5 w\\n0 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CO\\nCO\\nCM\\np-\\n^7\\nCO\\nCD\\nCO\\nCO\\nCM\\ngj S\\n.2 0\\nN N\\n03 C\\n-o _g\\nx 2\\no\\nx\\n0 y\\nE h=\\nD 4\\nD\\nc\\n03\\nCL\\nO\\nw_\\nCL\\nO\\n0\\nC\\nN\\nca\\nx\\nCM\\n0\\n\u00e2\u0080\u00a2g\\nx\\no\\n0\\nc\\n03\\nX\\nC/5\\nw\u00e2\u0080\u0094\\n03\\nCO\\n03\\n\u00e2\u0096\u00a0D\\nC\\n03\\ng\\n03\\nC/5\\nO)\\nc\\nD\\n_g\\no\\nc\\n*g\\n\u00e2\u0080\u0098o\\ng\\n03\\no\\n03\\nS\\nO\\nc\\n0)\\n13\\no\\nCL\\nQ LU\\nCM CM CM\\n03\\nC\\n03\\nCL\\no\\n03\\nC\\no\\n3\\n03\\nC\\n03\\nN\\nC\\n03\\nb\\n3\\nc\\n03\\nCL\\no\\nUJ\\nt\u00e2\u0080\u0094\\no\\nc\\n0\\n-C\\nCL\\no\\nc\\n0\\n-C\\nCL\\nCL\\n0\\nk_\\ng\\nr~\\n0\\nc\\n0\\nc\\n0\\n13\\nc\\nQ.\\nO\\nC/3\\n03\\n03\\n_Q\\nO\\n03\\ng\\nD\\nQ\\nO\\nO\\nO\\nk_\\no\\nO\\nb\\n0\\nJO\\nQ.\\nD\\ng\\nCD\\nO\\no\\nC\\naj\\nk_\\no\\nc\\nCO\\n03\\nE\\nO\\nx:\\ng\\nsz\\ng\\n^7\\n0\\nk\u00e2\u0080\u0094\\n0\\nrg\\nQ_\\nJZ\\nX\\nv_\\n1\\n\u00e2\u0080\u0099k_\\n\u00e2\u0080\u0099C\\ncm\\n3\\no\\no\\no\\no\\nH\\nCD\\nh-\\nO\\nO\\nCO\\nb\\nb\\nb\\nxr_\\n(C\\nLO\\nCD\\nQ\\nb\\nb\\ncb\\ncb\\ncb\\nrr\\ncm\\nCO\\n^7\\n^7\\n4\\n4\\n4^\\nT-\\nY\u00e2\u0080\u0094\\nY-\\ny-\\nY\u00e2\u0080\u0094\\ncm\\ncm\\ncm\\ncm\\ncm\\ncm\\nTO\\n03\\nC\\no\\nc\\n03\\nCL\\no\\n03\\nC3\\n03\\nO\\nr ,o y\\no\\nx\\n9\\nCM CM\\nn\\n0\\n___\\n03\\n0\\nO\\nc\\n03\\niz\\n03\\nO\\nO\\nO\\nCO\\n0\\nO\\nTD\\n0\\nX\\n0\\nX\\n0\\nc\\nt5\\nc\\n0\\nC\\nC\\n0\\nTD\\nN\\nc\\ng\\nCM\\nc\\n0\\nX\\nN\\nC\\n0\\nX)\\nc\\nc/3\\nX)\\n03\\nT5\\nCL\\nT3\\nX)\\nS\\ng\\n0\\nc\\n0\\nO\\n0\\nc\\nu\\nk_\\n0\\nXI\\nx:\\n0\\n0\\n0\\n0\\nS\\n0\\n0\\nX\\nX\\nX\\ng\\nE\\nE\\n0\\n0\\n0\\n9\\n9\\n9\\n2\\n2\\nCO\\nCO\\nCO\\n^7\\n^7\\nCO\\nCO\\nCO\\n^7\\n^7\\n^7\\n03\\nCO\\n03\\nC\\nO\\n_g\\no\\nc\\n03\\nc\\n03\\nN\\nC\\n03\\nX\\nO\\nN\\n03\\no\\nc\\nc n V\\n8 s\\n03\\nC\\n03\\nX\\nO\\nCL\\nO\\nq z z\\n\u00e2\u0080\u00a24 -4 *4 -4\\n0 3\\n\u00e2\u0096\u00a0g x\\n0\\nc\\n0\\nD T)\\n\u00e2\u0080\u00a2D 0\\nE c\\n3 2\\nX\\nQ.\\ng\\nc\\n0\\nE\\ntj .a\\n0 0\\n0\\n0\\n1\\nS\\n0 0\\n0\\nu\\n0 u\\n03\\n03 -g\\n*C *C\\nO\\nO 8\\nO C\\n\u00c2\u00abrf\\nC/5\\n*o\\nc\\no\\no\\nCL\\nE\\no\\nO\\nO\\nc\\n03\\n_C\\nC/3\\nCO\\n03\\nC\\nT3\\ng\\no\\nc\\ng\\n*c\\n03\\nO)\\nO\\nC\\naT\\nO\\nc\\nD\\no\\nCL\\nE\\no\\n03\\nC\\nO\\nC/3\\n03\\n03\\nE\\no\\nk\u00e2\u0080\u0094\\n03\\nc\\n03\\nN\\nC\\n03\\nX)\\n03\\nc\\n\u00e2\u0096\u00a0O\\n_D\\no\\nc\\n03\\nc\\n03\\nN\\nC\\n03\\nCD\\n7.0 Hazardous Air Pollutants 7-19", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0141.jp2"}, "142": {"fulltext": "Table 7-4 (continued)\\nNational Air Pollutant Emission Trends, 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0\\np\\nCO\\nd\\no\\nCO\\nCM\\no\\nCO\\nCM\\nCO\\nCO\\nLO\\nLO\\nCO\\nCD\\nCM\\nr^-\\nr\u00e2\u0080\u0094\\nCO\\nLO\\nCO\\nCD\\n111\\no\\no\\no\\np\\nCO\\no\\no\\np\\nCD\\no\\np\\nLO\\n^r\\nco\\ny\u00e2\u0080\u0094\\nco\\np\\nCD\\nCO\\nCM\\nT~\\nco\\nCM\\ny\u00e2\u0080\u0094\\nCM\\nCM\\no\\nLO\\nCM\\no\\nco\\nCD\\np\\nT\u00e2\u0080\u0094\\no\\nCM\\no\\no\\no\\np\\nco\\no\\nCO\\np\\nCM\\ny\u00e2\u0080\u0094\\no\\nCO\\nCD\\ny\u00e2\u0080\u0094\\no\\nO\\n03\\nk.\\no\\np\\no\\nco\\no\\no\\no\\nCO\\nCD\\no\\nCO\\no\\nCM\\np\\nY\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\n00\\no\\no\\no\\nCD\\nCO\\no\\no\\no\\no\\no\\nCO\\no\\no\\nd\\np\\no\\no\\no\\nCO\\nd\\no\\nT\u00e2\u0080\u0094\\no\\nCO\\ncb\\no\\nCD\\np\\no\\no\\no\\no\\nP-\\nh-\\ncb\\no\\no\\no\\n3\\nLU\\nCM\\nCM\\nCM\\nCO\\no\\nCD\\nCM\\nT\u00e2\u0080\u009c\\nCM\\n00\\nCD\\nQC\\ntr\\nCD\\nCO\\nCO\\np_\\nCM\\nco\\nCD\\ncm\\nT~\\no\\nCM\\nCM\\ny\u00e2\u0080\u0094\\nco\\np-\\no\\nCO\\nCD\\nY\u00e2\u0080\u0094\\nCM\\nCO\\nCO\\nCM\\nCO\\nco\\ny\u00e2\u0080\u0094\\nCO\\nCM\\nCO\\no\\nco\\n00\\nCM\\n00\\ny\u00e2\u0080\u0094\\nCM\\nTf\\nLO\\nCD\\np-\\no\\nLO\\nLO\\nLO\\np^\\nCM\\nLO\\np-\\nLO\\nY\u00e2\u0080\u0094\\nCO\\nLO\\nLO\\nCO\\nCD\\ny\u00e2\u0080\u0094\\np-\\nCM\\nCM\\nCM\\n3\\np-\\nCO\\nCO\\nco\\no\\no\\no\\nco\\nCD\\np-\\nCM\\no\\ny\u00e2\u0080\u0094\\nCM\\nCM\\ny\u00e2\u0080\u0094\\nQ\\n(D\\n00\\nLO\\n00\\nCO\\nCO\\no\\nIN\\nCM\\no\\nCD\\np-\\no\\no\\nCM\\np^\\ny\u00e2\u0080\u0094\\nCO\\no\\no\\nCM\\np-\\nCO\\nCO\\nCO\\nrr\\nco\\nco\\np\\nY\u00e2\u0080\u009c\\nCO\\ny\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\nLO\\nCM\\nCD\\no\\nCO\\nCO\\no\\nCO\\nCO\\nCD\\no\\no\\nCO\\nLO\\no\\no\\nLO\\nLO\\no\\no\\ny\u00e2\u0080\u0094\\no\\no\\nLO\\nY~\\nCO\\nCO\\ny\u00e2\u0080\u0094\\nLO\\nCM\\nl\u00e2\u0080\u0094\\no\\nco\\no\\nCO\\no\\ny-\\ny-\\no\\ncb\\ny\u00e2\u0080\u0094\\no\\no\\no\\ncb\\no\\nd\\np-\\nCM\\nY~\\no\\nCM\\no\\np-\\nT\u00e2\u0080\u0094\\no\\no\\no\\n2\\nCM\\no\\n(D\\nCD\\nCO\\nco\\nY\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\ny\\nCM\\nCO\\nCO\\nCO\\nY\u00e2\u0080\u0094\\no_\\ny\u00e2\u0080\u0094\\nCM\\nLO\\nCO\\nCO\\nIN\\nCD\\nLO\\nCM\\n03\\no\\ny\u00e2\u0080\u0094\\nIN\\ncm\\no\\ncb\\nP-\\nCL\\nCO\\nCM\\nLO\\nCM\\no\\nco\\nCD\\no\\nCM\\nLO\\nCD\\nCM\\nCO\\nCM\\nCO\\nT\u00e2\u0080\u0094\\np\\no\\np\\n^_\\no\\nco\\n03\\np\\no\\nLO\\nCO\\nCO\\nCO\\ny\u00e2\u0080\u0094\\nLO\\nCD\\no\\no\\nCM\\nCD\\nr\u00e2\u0080\u0094\\nCM\\nCO\\nCO\\nLO\\nY\u00e2\u0080\u0094\\no\\nCD\\nCO\\n03\\n03\\nCO\\nCO\\nCO\\n03\\no\\nCO\\nCD\\nCO\\np\\ny\\nCM\\no\\nCM\\nCM\\nCO\\nCD\\n03\\no\\nco\\nCO\\nCO\\n03\\n5\\nCM\\nO\u00e2\u0080\u0099\\ny\u00e2\u0080\u0094\\np\\nCO\\nLO\\np\\nLO\\nY-\\no\\nLO\\nY\u00e2\u0080\u0094\\nco\\nCM\\no\\nCD\\nCD\\nLO\\np-\\nCO\\nCM\\no\\no\\nCM\\nCO\\nCO\\nco\\no\\nCM\\nCO\\nLO\\nY\u00e2\u0080\u0094\\np\\no\\no\\nLO\\np\\n03\\no\\nIN\\no\\nco\\nCD\\no\\no\\nLO\\nCM\\no\\nco\\nLO\\nCM\\noo\\ny\u00e2\u0080\u0094\\n03\\no\\no\\no\\nCO\\nT\u00e2\u0080\u0094\\nCM\\no\\n03\\nT-\\nLO\\nCM\\no\\nCM\\no\\ncb\\nP-\u00e2\u0080\u0099\\nT-\\ny\u00e2\u0080\u0094\\no\\np^\\no\\ny\u00e2\u0080\u0094\\no\\no\\ncb\\nd\\ncb\\no\\no\\ncb\\no\\nCM\\nLO\\nib\\no\\no\\no\\no\\nCM\\nY\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\nCD\\no\\nCD\\no\\nCO\\nY\u00e2\u0080\u0094\\n3\\nCO\\nCM\\nY\u00e2\u0080\u0094\\n03\\nco\\nco\\nT~\\nCO\\n00\\nCO\\nco\\niO\\nCO\\n03\\nco\\ncm\\nLO\\ny\u00e2\u0080\u0094\\nco\\ncm\\ny\u00e2\u0080\u0094\\nCM\\ny\u00e2\u0080\u0094\\np\\n03\\nCO\\nCO\\n00\\n03\\no\\ny\u00e2\u0080\u0094\\nCO\\no\\no\\np\\nCO\\no\\no\\no\\n03\\no\\no\\nCO\\no\\np\\no\\no\\nCM\\no\\no\\no\\nL0\\n03\\no\\nCO\\nCO\\nLO\\nLO\\nY\u00e2\u0080\u0094\\no\\no\\no\\no\\nCO\\no\\no\\nLO\\nCM\\no\\nCM\\no\\n03\\nCM\\nco\\nCO\\nLO\\nLO\\n03\\nLO\\nCO\\nLO\\n03\\np\\nLO\\no\\nCM\\nCO\\nCM\\nCO\\nco\\no\\no\\n03\\nLO\\no\\no\\nCO\\np\\nL0\\nCM\\no\\nCO\\no\\n03\\n^r\\n03\\no\\no\\nco\\nY-\\nCM\\nLO\\no\\np\\nco\\np\\ny\u00e2\u0080\u0094\\nLO\\no\\ny\u00e2\u0080\u0094\\nCM\\nLO\\nCO\\n03\\nCO\\nco\\nCD\\nco\\nCM\\no\\nCO\\no\\nCM\\nCO\\no\\nCD\\nCO\\no\\no\\nCO\\nCO\\nCO\\nT-\\np\\nCM\\nco\\no\\ncq\\nq\\nLO\\n1\\nTf\\no\\nCO\\np\\nCO\\nCO\\nY\u00e2\u0080\u0094\\no\\nib\\np\\no\\np\\ncb\\nCO\\np\\nLO\\n03\\no\\no\\ncb\\nY\u00e2\u0080\u0094\u00e2\u0080\u0099\\nY\u00e2\u0080\u0094\\nco\\ncb\\no\\no\\ny\u00e2\u0080\u0094\\nCM\\ncb\\np\\no\\n03\\nCM\\nCO\\nco\\nLO\\nLO\\nCM\\nLO\\nCO\\no\\no\\nCO\\nCO\\nCD\\nO-\\nT\u00e2\u0080\u009c\\nco\\ny\u00e2\u0080\u0094\\nCM\\np\\nLO\\nCO\\nCM\\nCO\\nT\u00e2\u0080\u0094\\no\\nCM\\nCM\\n03\\nCO\\np\\nCM\\nLO\\np\\nco\\nco\\nco\\nco\\no\\nY\u00e2\u0080\u0094\\nco\\ncm\\ncm\\ny\\nLO\\nCM\\no\\nco\\np\\no\\nY\u00e2\u0080\u0094\\nY-\\nLO\\np\\n0\\nC\\n03\\nQ.\\nO\\nw_\\nQ.\\nO\\nx:\\no\\nc\\no\\n0\\nc\\n0\\ng\\n0\\no\\n03\\njo\\no\\nO\\n10\\nC\\n03\\nE\\ng\\n1\\no\\nk_\\nXI\\nO\\nC/D*\\nCL\\n0\\nc\\n0\\ng\\n0\\no\\ng\\nc\\n03\\nO)\\nk\u00e2\u0080\u0094\\no\\ng\\nU\\no\\ny\\no\\nn\\nb\\n03\\nx:\\nf.)\\no\\n1\\nCM\\n03\\nc\\no\\nc\\nk.\\n03\\nc\\nd\\nCO\\no\\nk_\\n0\\n0^\\n0\\nC/3\\nCL\\nUJ\\nI\\n0\\nCO\\nb\\nT~\\nZn\\nk-\\n0\\n03\\no\\n13\\n\u00e2\u0096\u00a0u\\nL.\\no\\n03\\nO\u00e2\u0080\u0099\\no\\nN\\nD\\no\\nc\\nc\\n13\\no\\n0\\nc\\n0\\ng\\nP C\\no\\nI\\n10\\n0\\nO\\n0\\n0\\nD\\no\\nr\\n0\\ng\\nE\\no\\nin\\n*o\\nCD\\nc\\nQ.\\nXI\\nc\\n03\\nk_\\nS\\n10\\n03\\nCO\\nE\\n0\\nn\\no\\n03\\nco\\n0\\n0.\\n0\\no\\n13\\n(T\\nXI\\n03\\no\\nX\\nCD\\n03\\no\\n2\\no\\no\\ns\\n0\\n0\\n0\\nx:\\nvy\\nx\\nD\\n10\\n03\\nc\\nCD\\nD\\nX\\n10\\n03\\nc\\n03\\no\\n03\\nc\\n03\\n03\\n_c\\nQ.\\n03\\nr\\n10\\no\\nD\\no\\nE\\nD\\nQJ\\n10\\nX\\no\\n0\\n1\\no\\n0\\nE\\n0\\n0\\nCO\u00c2\u00ac\\nCO\\nc\\n0\\nCl\\nin\\nc\\ng\\n0\\no\\nk.\\nc\\nE\\ng\\nc\\nO\\n0\\nco\\no\\ng\\n0\\no\\n10\\nE\\no\\nk.\\ng\\n\u00e2\u0080\u00a2k_\\no\\nJZ\\no\\n0\\nc\\n0\\n1\\nm\\n0\\nc\\nTO\\n0\\nc\\ng\\no\\no\\nN\\nY\\no\\no\\no\\nc\\nc\\nc\\no\\nD\\nc\\nD\\nZD\\no\\n03\\nk_\\n0\\n03\\nJO\\no\\ng\\n0\\nin\\nd\\nCL\\no\\nv_\\nQ.\\no\\nV\u00e2\u0080\u0094\\nCL\\no\\nk_\\nCL\\no\\nk.\\nc\\nd\\nc\\nd\\n10\\n03\\n0\\n0\\na?\\n2-\\n0\\np\\n03\\nk\u00e2\u0080\u0094\\n0\\n\u00e2\u0080\u0099c\\n0\\nD\\no\\ng\\no\\ng\\no\\nXI\\ng\\n\u00e2\u0080\u0098k_\\n0\\n\u00e2\u0080\u0098k_\\ng\\nCl\\nin\\nc\\nc\\nc\\nc\\nc\\n0\\np\\n\u00e2\u0080\u0098c\\n(2\\nCL\\n0.\\nCL\\nCL\\no\\no\\nQC\\nCO\\ns\\nCO\\nF\\ni=\\nF\\nF\\nF\\nF\\nF\\nF\\nZ)\\nX\\n6\\n6\\n0\\nc\\nE\\ng\\nd\\n0\\nc\\n0\\n4\\nc\\na\\nx:\\na.\\n03\\nTO\\nC\\n03\\nd\\na\\n03\\n10\\na)\\np\\ng\\nCO\u00c2\u00ac\\nCO\\nd\\nCO\\nCD\\no\\n03\\nc\\nD\\nO\\nE\\n03\\n03\\nE\\n0\\n(D\\n10\\nc\\n03\\n(D\\nCD\\nD\\nE\\nCD\\nO\\n0\\nJO\\ng\\n\u00e2\u0080\u0099co\\n03\\n(D\\nE\\no\\no\\nCD\\nJO\\n(0\\nD\\nD\\ng-\\n\u00e2\u0080\u0099c\\nXI\\no\\n03\\nc\\no\\nE\\nGO\\nD\\n13\\nC\\n03\\n03\\n13\\nD\\nJO\\nCO\\n03\\nCD\\nCD\\nC\\n03\\nXI\\ng\\n(D\\nO\\nv_\\nQ.\\nE\\n13\\nc\\n03\\nCO\\n03\\nc\\n03\\n\u00e2\u0096\u00a0c\\n03\\nO\\nc\\nD\\n0)\\n03\\nS\\n3 -9\\nS 2\\na)\\n0) CO\\nCD D\\nCO\\nc\\n*D\\no -o\\nco g\\no g\\nCD C\\nk_-\\nQ. CO\\nD\\n51\\nm 05\\n8\\nO)\\n5) i\u00e2\u0080\u0094\\n7-22 7.0 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0144.jp2"}, "145": {"fulltext": "DRAFT Do not quote, cite, or distribute.\\nNational Air Pollutant Emission Trends, 1900-1998\\nTable 7-5. Baseline NTI (1990 to 1993)\\n188 HAPs by State (Point, Area, On-road, and Non-road)\\n188-List HAP Emissions (tpy)\\nState\\nTotal\\nPOINT\\nAREA\\nMOBILE:\\nOn-Road\\nMOBILE:\\nNon-Road\\nAlabama\\n163,292\\n102,129\\n21,852\\n30,049\\n9,261\\nAlaska\\n101,454\\n2,740\\n91,932\\n5,310\\n1,473\\nArizona\\n51,295\\n18,029\\n11,692\\n13,157\\n8,418\\nArkansas\\n83,581\\n41,423\\n14,407\\n22,292\\n5,459\\nCalifornia\\n491,166\\n183,989\\n86,077\\n151,809\\n69,292\\nColorado\\n66,905\\n20,295\\n19,672\\n19,078\\n7,859\\nConnecticut\\n76,732\\n46,829\\n10,488\\n11,887\\n7,528\\nDelaware\\n17,274\\n10,174\\n1,985\\n3,590\\n1,525\\nDistrict of Columbia\\n6,583\\n693\\n1,530\\n2,981\\n1,379\\nFlorida\\n200,415\\n57,177\\n40,473\\n72,504\\n30,261\\nGeorgia\\n173,341\\n74,634\\n28,060\\n55,426\\n15,221\\nHawaii\\n14,850\\n1,886\\n3,315\\n6,803\\n2,845\\nIdaho\\n29,366\\n3,522\\n13,154\\n10,317\\n2,372\\nIllinois\\n245,986\\n114,079\\n37,523\\n67,656\\n26,728\\nIndiana\\n157,964\\n82,172\\n23,024\\n39,949\\n12,818\\nIowa\\n71,294\\n28,967\\n10,676\\n25,274\\n6,377\\nKansas\\n72,201\\n34,186\\n10,949\\n21,327\\n5,739\\nKentucky\\n118,633\\n57,740\\n17,522\\n34,715\\n8,656\\nLouisiana\\n166,927\\n111,097\\n18,764\\n27,307\\n9,759\\nMaine\\n45,066\\n22,696\\n10,507\\n8,967\\n2,896\\nMaryland\\n70,763\\n21,631\\n13,297\\n24,745\\n11,089\\nMassachusetts\\n84,371\\n28,126\\n17,990\\n24,140\\n14,116\\nMichigan\\n214,078\\n100,887\\n35,290\\n56,267\\n21,635\\nMinnesota\\n94,113\\n29,861\\n21,731\\n32,260\\n10,260\\nMississippi\\n88,063\\n39,737\\n15,853\\n26,576\\n5,898\\nMissouri\\n135,396\\n59,561\\n22,888\\n40,733\\n12,214\\nMontana\\n31,037\\n6,186\\n14,938\\n8,027\\n1,887\\nNebraska\\n34,778\\n10,816\\n6,242\\n14,041\\n3,679\\nNevada\\n19,118\\n4,130\\n4,549\\n7,497\\n2,941\\nNew Hampshire\\n24,909\\n9,869\\n5,327\\n7,135\\n2,578\\nNew Jersey\\n172,543\\n106,049\\n21,108\\n27,488\\n17,897\\nNew Mexico\\n35,493\\n7,027\\n10,637\\n14,276\\n3,552\\nNew York\\n267,090\\n94,383\\n52,425\\n78,483\\n41,798\\nNorth Carolina\\n173,488\\n77,075\\n28,089\\n52,870\\n15,453\\nNorth Dakota\\n16,738\\n4,860\\n4,545\\n5,837\\n1,497\\nOhio\\n256,532\\n125,774\\n38,453\\n67,255\\n25,049\\nOklahoma\\n73,465\\n23,377\\n15,709\\n27,110\\n7,269\\nOregon\\n74,757\\n27,695\\n21,023\\n19,305\\n6,734\\nPennsylvania\\n227,812\\n102,692\\n39,771\\n57,595\\n27,755\\nRhode Island\\n17,562\\n6,718\\n3,134\\n5,367\\n2,342\\nSouth Carolina\\n107,593\\n60,878\\n15,381\\n23,315\\n8,019\\nSouth Dakota\\n15,272\\n2,659\\n3,649\\n7,344\\n1,619\\nTennessee\\n195,631\\n126,355\\n21,835\\n36,132\\n11,309\\nTexas\\n506,367\\n285,785\\n67,534\\n113,157\\n39,891\\nUtah\\n104,117\\n77,457\\n11,191\\n11,391\\n4,078\\nVermont\\n11,928\\n1,371\\n3,307\\n5,928\\n1,321\\nVirginia\\n148,893\\n63,274\\n25,209\\n45,815\\n14,595\\nWashington\\n133,232\\n67,143\\n23,960\\n30,509\\n11,620\\nWest Virginia\\n84,607\\n52,172\\n10,838\\n17,478\\n4,118\\nWisconsin\\n125,329\\n57,360\\n21,349\\n35,349\\n11,271\\nWyoming\\n16,350\\n3,960\\n6,547\\n4,747\\n1,096\\nNote(s): The estimates included in these tables have uncertainties and will in-\\nbecome available over time.\\niprove/change as better data and estimation techniques\\nHazardous Air Pollutants 7-23", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0145.jp2"}, "146": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nDRAFT Do not quote, cite, or distribute.\\nTable 7-6. Baseline NTI (1990 to 1993)\\n33 HAPs by State (Point, Area, On-road, and Non-road)\\n33 Urban HAP Emissions (tpv)\\nState\\nTotal\\nPOINT\\nAREA\\nMOBILE:\\nOn-Road\\nMOBILE:\\nNon-Road\\nAlabama\\n31,634\\n9,694\\n11,482\\n7,226\\n3,231\\nAlaska\\n69,102\\n610\\n66,610\\n1,277\\n606\\nArizona\\n14,933\\n2,290\\n6,525\\n3,163\\n2,955\\nArkansas\\n20,631\\n4,594\\n8,736\\n5,361\\n1,940\\nCalifornia\\n125,546\\n29,954\\n34,308\\n36,507\\n24,777\\nColorado\\n23,384\\n3,083\\n12,817\\n4,588\\n2,896\\nConnecticut\\n15,178\\n5,973\\n3,719\\n2,859\\n2,627\\nDelaware\\n3,138\\n1,065\\n684\\n863\\n526\\nDistrict of Columbia\\n1,932\\n257\\n480\\n717\\n477\\nFlorida\\n53,073\\n8,233\\n16,531\\n17,436\\n10,873\\nGeorgia\\n43,658\\n10,016\\n14,807\\n13,329\\n5,507\\nHawaii\\n4,577\\n378\\n1,432\\n1,636\\n1,131\\nIdaho\\n14,209\\n636\\n10,231\\n2,481\\n861\\nIllinois\\n51,251\\n12,365\\n13,003\\n16,270\\n9,612\\nIndiana\\n35,442\\n12,577\\n8,769\\n9,607\\n4,490\\nIowa\\n15,161\\n3,065\\n3,779\\n6,078\\n2,240\\nKansas\\n16,293\\n5,500\\n3,659\\n5,129\\n2,004\\nKentucky\\n25,314\\n4,826\\n9,026\\n8,348\\n3,114\\nLouisiana\\n28,369\\n9,740\\n8,624\\n6,567\\n3,438\\nMaine\\n14,483\\n3,196\\n8,086\\n2,157\\n1,045\\nMaryland\\n17,841\\n3,013\\n4,931\\n5,951\\n3,946\\nMassachusetts\\n23,015\\n5,122\\n6,985\\n5,805\\n5,103\\nMichigan\\n49,053\\n11,437\\n16,397\\n13,531\\n7,688\\nMinnesota\\n25,884\\n4,095\\n10,349\\n7,758\\n3,682\\nMississippi\\n22,873\\n5,476\\n8,958\\n6,391\\n2,048\\nMissouri\\n31,750\\n6,778\\n10,661\\n9,796\\n4,515\\nMontana\\n14,775\\n800\\n11,366\\n1,930\\n680\\nNebraska\\n7,442\\n836\\n1,929\\n3,377\\n1,300\\nNevada\\n5,733\\n553\\n2,253\\n1,803\\n1,124\\nNew Hampshire\\n7,489\\n1,639\\n3,215\\n1,716\\n919\\nNew Jersey\\n27,161\\n7,282\\n6,910\\n6,610\\n6,358\\nNew Mexico\\n11,931\\n904\\n6,316\\n3,433\\n1,278\\nNew York\\n71,368\\n17,392\\n20,171\\n18,874\\n14,932\\nNorth Carolina\\n41,541\\n8,996\\n14,293\\n12,714\\n5,537\\nNorth Dakota\\n3,292\\n394\\n960\\n1,404\\n534\\nOhio\\n54,289\\n15,569\\n13,721\\n16,174\\n8,825\\nOklahoma\\n20,979\\n4,260\\n7,644\\n6,520\\n2,556\\nOregon\\n25,797\\n4,361\\n14,346\\n4,643\\n2,448\\nPennsylvania\\n54,091\\n14,288\\n15,979\\n13,850\\n9,974\\nRhode Island\\n3,996\\n646\\n1,220\\n1,291\\n839\\nSouth Carolina\\n22,818\\n6,825\\n7,571\\n5,607\\n2,815\\nSouth Dakota\\n3,936\\n233\\n1,358\\n1,766\\n580\\nTennessee\\n29,904\\n7,110\\n10,096\\n8,689\\n4,009\\nTexas\\n95,759\\n28,265\\n25,913\\n27,212\\n14,369\\nUtah\\n12,322\\n2,273\\n5,821\\n2,739\\n1,488\\nVermont\\n4,439\\n247\\n2,288\\n1,426\\n479\\nVirginia\\n35,320\\n6,153\\n12,852\\n11,018\\n5,297\\nWashington\\n36,234\\n10,519\\n14,123\\n7,337\\n4,255\\nWest Virginia\\n15,959\\n3,873\\n6,443\\n4,203\\n1,441\\nWisconsin\\n29,971\\n7,156\\n10,355\\n8,501\\n3,959\\nWyoming\\n7,145\\n290\\n5,325\\n1,141\\n389\\nbecome available over time.\\n7-24 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0146.jp2"}, "147": {"fulltext": "DRAFT Do not quote, cite, or distribute.\\nNational Air Pollutant Emission Trends, 1900-1998\\nTable 7-7. Baseline NTI (1990 to 1993)\\n33 HAPs by Tier 1\\nEmissions (tpy) for Tier 1 Reporting Levels\\n01\\n02\\n03\\n04\\n05\\n06\\n07\\nFUEL\\nCHEMICAL\\nCOMB.\\nFUEL\\nFUEL\\nALLIED\\nPETROLEUM\\nOTHER\\nELEC.\\nCOMB.\\nCOMB.\\nPRODUCT\\nMETALS\\nRELATED\\nINDUSTRIAL\\nNTI Pollutant Description\\nUTIL.\\nINDUSTRIAL\\nOTHER\\nMFG\\nPROCESSING\\nINDUSTRIES\\nPROCESSES\\n1,1,2,2-Tetrachloroethane\\n0.00000\\n0.00000\\n0.00000\\n17.78800\\n0.51700\\n0.01850\\n11.32150\\nEthylene Dichloride\\n27.02126\\n0.81934\\n0.13473\\n2,898.72120\\n0.00190\\n91.81822\\n1,105.11616\\nPropylene Dichloride\\n0.00000\\n0.00001\\n0.00000\\n428.43400\\n0.00000\\n0.66500\\n201.84800\\n1,3-Butadiene\\n0.51750\\n48.74947\\n0.94777\\n3,277.96648\\n530.13000\\n152.43093\\n11.48258\\nAcetaldehyde\\n65.84379\\n2,300.74122\\n33.14230\\n6,657.73027\\n2.80059\\n61.96659\\n13,321.32602\\nAcrolein\\n28.55861\\n8.71325\\n1.33634\\n397.40819\\n11.10208\\n2.17710\\n308.81792\\nAcrylonitrile\\n0.00042\\n0.00000\\n0.00000\\n2,054.03964\\n0.62600\\n46.36117\\n24.34623\\nArsenic Compounds\\n(inorganic including arsine)\\n61.48658\\n13.52304\\n7.44388\\n3.06196\\n106.28059\\n40.55300\\n44.21509\\nBenzene\\n37.84816\\n1,037.31036\\n32.46966\\n5,079.51076\\n2,771.11883\\n25,830.05279\\n2,076.41741\\nBeryllium Compounds\\n7.17599\\n0.78875\\n2.10119\\n0.00056\\n0.91142\\n0.26163\\n0.90331\\nCadmium Compounds\\n4.00910\\n2.80706\\n3.10371\\n9.22847\\n131.77837\\n6.60694\\n15.72217\\nCarbon tetrachloride\\n0.00613\\n0.01472\\n0.00032\\n637.27465\\n0.00000\\n48.48671\\n4,282.45080\\nChloroform\\n0.00540\\n0.03079\\n0.00986\\n1,746.31005\\n0.32800\\n1.78696\\n20,444.24719\\nChromium Compounds\\n76.64199\\n14.50598\\n7.02827\\n68.45539\\n137.89791\\n42.98149\\n431.04281\\nCoke Oven Emissions\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n826.73000\\n0.00000\\n0.00000\\nEthylene Dibromide\\n0.00314\\n0.00345\\n0.00014\\n28.80755\\n0.00007\\n11.14484\\n7.38021\\nEthylene Oxide\\n0.00000\\n0.00000\\n0.00000\\n949.76887\\n0.00000\\n9.11563\\n585.64322\\nFormaldehyde\\n198.76632\\n26,223.73958\\n685.19718\\n3,285.17222\\n134.38944\\n753.11352\\n9,829.56747\\nHexachlorobenzene\\n0.00000\\n0.00010\\n0.00002\\n1.43850\\n0.00000\\n0.00000\\n0.00001\\nHydrazine\\n0.00000\\n0.00000\\n0.10511\\n15.51250\\n0.50250\\n3.28905\\n0.63904\\nLead Compounds\\n87.08918\\n30.14759\\n17.83845\\n181.47978\\n839.68597\\n47.17316\\n552.67951\\nManganese Compounds\\n192.16294\\n547.20368\\n245.54949\\n222.08554\\n1,187.28718\\n50.00145\\n357.28506\\nMercury Compounds\\n53.28055\\n2.92661\\n3.13193\\n13.41729\\n3.45209\\n1.46299\\n10.53589\\nMethylene chloride\\n119.63081\\n9.09658\\n1.39897\\n45,291.70359\\n217.60550\\n29.39032\\n34,111.13747\\nNickel Compounds\\n450.48274\\n125.73762\\n120.67300\\n20.22190\\n88.27336\\n111.05618\\n253.55360\\nPolychlorinated biphenyls\\n0.00001\\n0.00499\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00943\\n16-PAH\\n8.81088\\n218.44557\\n73.99793\\n865.61650\\n1,947.12400\\n1,317.14250\\n1,288.75071\\nTetrachloroethylene\\n27.50444\\n1.29597\\n0.38331\\n668.97825\\n396.59375\\n17.88168\\n6,857.57749\\nTrichloroethylene\\n0.19297\\n7.53408\\n0.73649\\n383.98201\\n952.72172\\n67.64605\\n12,332.57601\\nVinyl chloride\\n0.08442\\n0.68360\\n0.05934\\n2,154.41688\\n0.00000\\n4.65101\\n16.80269\\n1,3-Dichloropropene\\n0.00000\\n0.00000\\n0.00000\\n30.29300\\n0.78700\\n0.00000\\n0.00000\\nQuinoline\\n0.00000\\n0.00000\\n0.00000\\n12.49950\\n9.06150\\n4.37950\\n0.08500\\n2,3,7,8-TCDD TEQ\\n0.00011\\n0.00009\\n0.00004\\n0.00000\\n0.00020\\n0.00000\\n0.00007\\nNote(s): EPA uses a data base to store these emissions. Since the data base stores very large and very small amounts, the number of decimal\\nplaces displayed are an artifact of that storage and are not intended to suggest true precision of large values.\\nThe estimates included in these tables have uncertainties and will improve/change as better data and estimation techniques become\\navailable over time.\\nHazardous Air Pollutants 7-25", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0147.jp2"}, "148": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nDRAFT Do not quote, cite, or distribute.\\nTable 7-7 (continued)\\nEmissions (tpy) for Tier 1 Reporting Levels\\n08\\n09\\n10\\n11\\n12\\n13\\n14\\nWASTE\\nSOLVENT\\nSTORAGE\\nDISPOSAL\\nHIGHWAY\\nOFF-\\nNATURAL\\nNTI Pollutant Description\\nUTILIZATION\\nTRANSPORT\\nRECYCLING\\nVEHICLES\\nHIGHWAY\\nSOURCES\\nMISC.\\n1,1,2,2-Tetrachloroethane\\n0.00000\\n0.00000\\n218.92334\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\nEthylene Dichloride\\n16.42611\\n7.48812\\n50.46048\\n0.00000\\n0.00000\\n0.00000\\n0.59675\\nPropylene Dichloride\\n0.00000\\n0.00000\\n24.04231\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n1,3-Butadiene\\n0.04703\\n24.35674\\n4.43295\\n36,657.97824\\n10,887.12866\\n0.00000\\n19,927.39934\\nAcetaldehyde\\n6.82552\\n0.05892\\n20.97927\\n27,963.87210\\n37,330.86678\\n0.00000\\n49,400.00000\\nAcrolein\\n1.01533\\n0.01852\\n24.12055\\n5,541.61622\\n6,729.03608\\n0.00000\\n49,606.34473\\nAcrylonitrile\\n2.26141\\n0.07673\\n415.88935\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\nArsenic Compounds\\n(inorganic including arsine)\\n0.01758\\n0.57411\\n7.78977\\n1.74759\\n1.04001\\n0.00001\\n0.69877\\nBenzene\\n278.28297\\n11,967.59638\\n629.87446\\n207,259.79811\\n72,411.29730\\n0.00000\\n59,936.33896\\nBeryllium Compounds\\n0.00463\\n0.00435\\n0.17002\\n0.00000\\n0.02000\\n0.00000\\n0.05160\\nCadmium Compounds\\n0.91489\\n0.08872\\n24.37846\\n0.02668\\n0.31011\\n0.00003\\n0.14613\\nCarbon tetrachloride\\n0.43361\\n1.68034\\n70.03906\\n0.00000\\n0.00000\\n0.00000\\n0.12523\\nChloroform\\n7.04926\\n1.76505\\n409.65664\\n0.00000\\n0.00000\\n0.00000\\n124.09405\\nChromium Compounds\\n51.91006\\n0.11269\\n12.39676\\n27.93068\\n25.83012\\n0.00038\\n0.41570\\nCoke Oven Emissions\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n936.96000\\nEthylene Dibromide\\n4.97356\\n1.79958\\n3.42732\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\nEthylene Oxide\\n12.93591\\n0.03810\\n13.95000\\n0.00000\\n0.00000\\n0.00000\\n1,190.29814\\nFormaldehyde\\n733.66738\\n4.94350\\n27.75885\\n96,816.50994\\n79,405.52602\\n0.00000\\n129,228.16239\\nHexachlorobenzene\\n0.00000\\n0.00000\\n0.00004\\n0.00000\\n0.00000\\n0.00000\\n0.14600\\nHydrazine\\n0.31678\\n0.09795\\n0.00002\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\nLead Compounds\\n76.84471\\n4.82841\\n270.92826\\n418.03935\\n778.25807\\n0.00019\\n2.14997\\nManganese Compounds\\n29.59095\\n5.58907\\n11.72747\\n21.68763\\n30.34058\\n0.00210\\n8.40762\\nMercury Compounds\\n0.01422\\n0.05540\\n103.12032\\n4.96458\\n6.93002\\n1.30002\\n1.36043\\nMethylene chloride\\n37,708.01972\\n18.39548\\n2,125.70399\\n0.00000\\n16.90000\\n0.00000\\n4,636.51936\\nNickel Compounds\\n35.68361\\n0.14186\\n28.06791\\n15.54908\\n79.33141\\n0.00011\\n0.75751\\nPolychlorinated biphenyls\\n0.00014\\n0.00102\\n0.03399\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n16-PAH\\n2,038.45400\\n729.08450\\n97.94350\\n75.93000\\n33.29000\\n0.00000\\n8,570.59160\\nTetrachloroethylene\\n115,418.70645\\n17.23776\\n1,000.83989\\n9.50000\\n77.40000\\n0.00000\\n3,506.81301\\nTrichloroethylene\\n57,683.51050\\n3.69705\\n455.64005\\n0.00000\\n0.00000\\n0.00000\\n110.41250\\nVinyl chloride\\n0.61149\\n0.00001\\n534.77648\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n1,3-Dichloropropene\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n19,896.79000\\nQuinoline\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n0.00000\\n2,3,7,8-TCDD TEQ\\n0.00000\\n0.00000\\n0.00194\\n0.00009\\n0.00000\\n0.00000\\n0.00009\\nNote(s): EPA uses a data base to store these emissions. Since the data base stores very large and very small amounts, the number of decimal\\nplaces displayed are an artifact of that storage and are not intended to suggest true precision of large values.\\nThe estimates included in these tables have uncertainties and will improve/change as better data and estimation techniques become\\navailable over time.\\n7-26 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0148.jp2"}, "149": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\no\\no\\no\\nCO\\nI s CO\\no\\nCO\\ny-\\no\\no\\nn-\\ny-.\\ny-.\\nco\\nOD\\no\\no\\noo\\nCO\\nCM\\no\\nO\\n0\\nO\\n0\\n0\\nCD\\nO\\n0\\n0\\nCO\\n4\\n0\\nco\\nCO\\n00\\nO\\n0\\n0)\\nlO\\nT\u00e2\u0080\u0094\\no\\no\\nco\\no\\n03\\nCD\\noo\\nr-\\nr-\\nCO\\nco\\nco\\nCD\\nCD\\nCD\\nin\\nCD\\nCD\\n0\\nCD\\n0\\nCD\\n0\\n0\\n0\\nOD\\n00\\n0\\nco\\nin\\nC D\\nCM\\nC\\nr-\\no\\no\\no\\nI s\\nCD 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_\\nra\\nO\\nI\u00e2\u0080\u0094\\no\\n1\\nCD\\nra\\nL_\\nO\\n4\u00e2\u0080\u0094*\\nIf)\\n4-*\\no\\n3\\n\u00e2\u0080\u009cO\\n2\\n0\\nE\\n3\\nra\\no\\nL_\\n0\\nCL\\nE\\nra\\nra\\no\\ni\u00e2\u0080\u0094\\nra\\nCl\\n\u00e2\u0096\u00a0c\\no\\nCL\\nCO\\nc\\nra\\no\\nra\\nO\\no\\nCO\\nc\\nQ.\\nE\\nLU\\n\u00c2\u00b0S\\nCO\\nc\\nCL _ .2\\nc ra ra\\n0 0\\nra 2 2\\nra\\nco\\n03\\nL_\\no\\nto co m\\nco S\\no E\\n-C\\nco O\\nra 2\\no c\\nra\\n05\\nCD X\\nCO O\\nCD\\nCO CO\\nc c\\no o\\nro ra\\n4\u00e2\u0080\u0094* 4\u00e2\u0080\u0094\u00e2\u0080\u0099\\n3 CO CO\\nra o\\n-5 .2 .2\\nra ra ra\\n0. CO CO\\nO O)\\no. ra\\nw 2\\n5 co\\nL ra\\nra o\\n\u00e2\u0080\u00a2F E\\nE ra\\nra -c\\n-3 O\\nO o\\n.2 c\\nc ra\\nra o)\\nE\u00c2\u00bb o\\nO\\nO\\nO\\no\\nLU\\nO) oc\\n2 oa\\nQ\\nCO\\nco CO\\nra O\\n\u00e2\u0080\u00a2o 0\\nco\\nQ\\n_ LU\\nco\\nra\\nw_\\no\\nO)\\nra\\n4\u00e2\u0080\u0094*\\nra\\nO\\nI\u00e2\u0080\u0094\\no\\nO)\\nsi\\n2 m\\no c\\n.2 ra\\no CL\\nO\\nra\\nra\\ni\\nra\\n4\u00e2\u0080\u0094*\\n0\\n03\\n03\\nCO\\n3\\n\u00e2\u0096\u00a0o\\nc\\n_co\\nQ 1\\nco ra\\nco\\nLU\\n_i\\no\\nI\\nLU\\nX\\nCD\\nII\\nX O\\nCO\\nLU\\no\\nCC\\n3\\nO\\nCO\\n_J\\nX\\nX w\\n0\\no\\nc\\nra\\nO)\\no\\nra\\nCM\\nCO\\nt\\nm\\nCD\\nr-\\nco\\nCD\\n0\\n0\\nT\u00e2\u0080\u0094\\nCM\\nCO\\nm\\nco\\n0\\nT-\\nCM\\nCO\\n\u00e2\u0080\u00a2M-\\nm\\nCD\\nI s\\n00\\nCD\\nO\\nCM\\nLO\\nCO\\n0\\nO\\n0\\n0\\n0\\n0\\n0\\nO\\nq\\nO\\nO\\nO\\n0\\n0\\n0\\n0\\nO\\nO\\nO\\nO\\n0\\nO\\nO\\nO\\nO\\ny\u00e2\u0080\u0094\\nq\\nq\\nq\\nq\\nq\\nq\\nI s\\nr-^\\nr-\\nr-\\n1^\\n1^\\nr-:\\nco\\ncd\\n00\\n00\\nco\\n00\\nco\\ncd\\nCD\\nCD\\nCD\\nCD\\nCD\\nO)\\nCD\\nCD\\nCD\\nCD\\nCD\\n03\\n0 0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\nO\\nO\\n0\\n0\\n0\\n0\\n0\\n0\\nO\\nO\\nO\\nO\\n0\\nO\\nO\\nO\\nO\\nO\\ny\\nCM\\no\\nCM CO CO\\n7-28 7.0 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0150.jp2"}, "151": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n\u00e2\u0096\u00a0o\\nD\\n3\\nC\\nc\\no\\n00\\nI\\nr^-\\n0)\\nn\\nco\\nH\\nQ.\\n4-^\\n(0\\nc\\no\\n\u00e2\u0080\u009835\\n2\\nuj\\na)\\nc\\n0\\nT3\\n0\\n4\\n3\\nCQ\\nCO\\nw\\nII\\nu\\nCQ 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E\\n2 w\\n0\\nO 0)\\nc x:\\n0 I\u00e2\u0080\u0094\\n7.0 Hazardous Air Pollutants 7-29", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0151.jp2"}, "152": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n~o\\nD\\nZ3\\nC\\n\u00e2\u0080\u00a24-\\nc\\no\\n00\\nr-\\n0\\nJQ\\n(0\\nK\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nO\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nO\\nCM\\nCD\\no\\no\\nCD\\no\\no\\no\\no\\no\\no\\no\\no\\nn\\nO 01\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nCO\\nCD\\no\\no\\nCM\\no\\no\\no\\no\\no\\no\\no\\no\\nco\\nC 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B\\nCD\\nCD\\n03\\n0\\n3\\nc n\\n4\u00e2\u0080\u0094\\no\\n3\\nO\\no\\n0\\n0\\n3\\no\\no\\n(2 Q\\nCD 2?\\nc\\nCD\\nE\\n3\\n_ C/2\\no 05 c\\nO 3 o\\nO ll O\\nX\\n3\\nCL\\n\u00c2\u00b03\\nC\\no\\n5\\no w\\n8. g\\nc\\nCD s\\nCD\\nO\\nw\\n3\\no\\nCD\\nc\\n_ra\\n0\\no\\nw\\n2 CD\\nI- C/5\\ni-wn^incoNT-ooco\\nqqqqqqocM^r -q\\nTt Tf Tt rf Tf Tt Tt Tt Tt Tt\\n0\\nCD\\n5\\nO\\nCO\\nc3\\nJO\\no\\nr\\n0\\nc\\n0\\n0\\nL_\\n0\\n~o\\n0\\n0\\nCL\\n0\\nd\\n0\\n0\\nO\\n_0\\nCL\\n\u00e2\u0080\u009c0\\nE\\no\\n0\\nTD\\n0\\n-Q\\nE\\n3\\nC\\n0\\n0\\n4\u00e2\u0080\u0094*\\nC\\n3\\nO\\nE\\nCD\\n0\\nE\\nCO\\nCD\\n~0\\nC\\nCD\\nCD\\n0)\\nk_\\n_0\\nCD\\nCO\\nCD\\nCD\\nCO\\nCD\\nX\\nCD\\nE\\nCD\\nO\\n_0\\nX\\n0\\n5\\nCD\\nCD\\nE\\ng\\nCD\\nX\\nCO\\n0\\n3\\ng-\\nc\\nx\\no\\n0\\n4\u00e2\u0080\u0094*\\nc\\no\\n0\\nE\\n4\u00e2\u0080\u0094 1\\n0\\n0\\nO\\nc\\n0\\n0\\n4\u00e2\u0080\u0094\\n0\\n\u00e2\u0080\u009cO\\n0\\ntz\\n0\\n3\\n0\\n0\\n0\\nCD\\nC\\n0\\nSZ\\n~0\\no\\nL_\\nQ.\\nE\\nCD\\n0\\no\\nc _\\nCO JS\\nCO 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o\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nC3\\no\\no\\no\\no\\no\\no\\no\\no\\no\\noooooooooooooooo\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no o o o o o\\no o o o\\no o o o\\no o o o\\no o o o\\no o o o\\ndodo\\nC/3\\n8 \u00c2\u00a32\\n-O o\\nO n\\nCL o\\n03\\np\\no 2\\n5\\nD\\nCL\\nc/3\\n03\\nC/3\\nCO\\n33\\no\\no\\nr\\n\u00c2\u00b08\\n0\\nD\\no\\np CD\\n2 c\\n9- 03\\nCL 03\\no\\n08 C/3\\nO- is\\n3\\n0.\\nOQ\\n\u00e2\u0096\u00a0g J\u00c2\u00a7\\nJs\\nCL\\n0\\no\\nD\\n~o\\no\\nL_\\nCL\\n0\\nL_\\n0\\nc\\nE\\n-O 9\\nO 3\\nw\\n2\\n03 C\\nc o\\n_C d\\no O\\nCO 0\\n2 CD\\nc\\n03\\nE\\ng.\\n3\\nCT\\nID\\nc\\n.9 c\\n0 0\\nC t$\\nQ-\\n\u00c2\u00ab2 w\\n5 c\\n5 o\\nI- 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i\u00e2\u0080\u0094\\n7.0 Hazardous Air Pollutants 7-35", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0157.jp2"}, "158": {"fulltext": "National Air Pollutant Emission Trends 1900-1998\\n\u00e2\u0096\u00a0Q\\nD\\n3\\nC\\n4-\u00c2\u00bb\\nc\\no\\nO\\n00\\nI\\nr-\\nQ)\\nJD\\n0\\nQ\\nc\\no\\nw\\nE\\nUJ\\n0\\nc\\no\\nc\\nd\\nO\\no\\no V\\nTO\\n\u00c2\u00a3-2\\nc\\nO CO\\nQ. 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CO\\nt\\nCD\\no\\n05\\nO)\\nQ.\\n03\\nc\\nk_\\no\\no\\n03\\nk_\\n4\u00e2\u0080\u00941\\nCO\\nCO\\n15\\no\\n15\\no\\no\\nE\\nE\\nE\\n0\\nCD\\n0\\n-C\\n-C\\n-C\\no\\no\\no\\no\\no\\no\\n\u00e2\u0080\u0098c\\n\u00e2\u0080\u0099c\\n\u00e2\u0080\u0099c\\n0\\n03\\n03\\no\\nO)\\nv_\\nO)\\nL\u00e2\u0080\u0094\\no\\no\\no\\nc\\n05\\nco\\no\\nCO\\n(0\\n.2\\n3\\nCO\\n0\\no\\no\\n111\\nQC\\n\u00c2\u00b08\\nco\\nV)\\n05\\nC\\n4\u00e2\u0080\u0094 1\\nCO\\n03\\nCO o\\nO CD\\nCL C\\nCD p\\nQ V\\n111\\no\\nCO\\nCO\\nk_\\nc\\nCO c\\nC CO U-\\nQ\\no q. o m\\nO h\\nCO\\nHI\\n_i\\nO\\nI\\nHI\\nO\\nc _c\\n^3 6\\nX\\n0\\nX\\n0\\nHI\\no\\nX\\n3\\no\\nCO\\n_J\\nX\\n3\\n2 11\\no\\nc\\n05\\nO\\n0\\nCM\\nCD\\n\u00e2\u0096\u00a0M-\\nLD\\nCD\\nr-\\noo\\n05\\no\\no\\n1\u00e2\u0080\u0094\\nCM\\nCD\\n\u00e2\u0080\u00a2M\\nLD\\nCD\\nO\\n^_\\nCM\\nCD\\n\u00e2\u0080\u00a2M-\\nID\\nCO\\nr-\\n00\\nCT\\no\\neg\\no\\no\\no\\no\\no\\no\\no\\no\\nT\u00e2\u0080\u0094\\no\\no\\no\\no\\no\\nO\\nO\\no\\no\\nO\\nO\\nO\\nO\\nO\\no\\no\\no\\nT\u00e2\u0080\u0094\\no\\nq\\no\\n1^\\nr-\\nr-^\\n1^\\n1^\\nr-:\\n1^\\nK\\nr-^\\noo\\ncd\\ncd\\nco\\noo\\noo\\n00\\nCO\\n05\\n05\\n05\\n05\\n05\\n05\\n05\\n05\\n05\\nCT)\\nCT\\nCT\\no o\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nO\\nO\\nO\\nO\\nO\\nO\\nO\\nO\\nO\\no\\no\\no\\nO\\ny\u00e2\u0080\u0094\\nID CO\\nO O O\\no\\no o o o\\nCM\\nO\\nCM CO CD\\n7-40 7.0 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0162.jp2"}, "163": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nT3\\nD\\n3\\nc\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094\\nc\\no\\n00\\nI\\nr^\\n.Q\\n(0\\nQ\\n(0\\nc\\no\\nw\\nE\\nLU\\n0)\\nk.\\no\\nCT\\nO\\nc\\nC\\nCT\\n0)\\no\\nct\\no\\n0)\\nc\\nD\\nct\\n0)\\no\\nCT\\no\\nTO\\nk-\\nk\u00e2\u0080\u0094\\n.4)\\n*2\\ncm ra\\nct\\nT- 0)\\no\\nCT\\no\\nro\\nk.\\nA x\\nO o\\nN\\nC CT\\nD\\nCT\\nct\\no\\nA\\no\\nfO\\nk_\\no\\nO\\n0)\\n0)\\nA\\nE\\nO 0\\noooooooooooo\\noooooooooooo\\noooooooooooo\\noooooooooooo\\noooooooooooo\\noooooooooooo\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nIf)\\no\\no\\no\\no\\no\\no\\no\\nin\\nin\\no\\nLO\\nC\\\\J\\no\\no\\no\\no\\no\\no\\no\\nCO\\nin\\n03\\nT\u00e2\u0080\u0094\\no\\no\\no\\no\\no\\no\\no\\nCO\\no\\nC\\\\J\\no\\no\\no\\no\\no\\no\\no\\no\\nLO\\no\\no\\no\\no\\nd\\no\\no\\no\\no\\nd\\nco\\nT-i\\nco\\nCO\\nI\\nT\u00e2\u0080\u0094\\no\\no\\no\\no\\no\\no\\no\\nT-\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nM\\n00\\no\\no\\nCO\\no\\no\\no\\no\\no\\no\\no\\nO)\\nco\\no\\no\\ny\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nco\\no\\no\\no\\no\\no\\no\\no\\noo\\no\\no\\no\\nd\\no\\no\\no\\no\\no\\no\\no\\ncd\\no\\no\\nd\\no\\nIf)\\n00\\no\\nIf)\\nCO\\no o o o\\no o o o\\no o o o\\no o o o\\no o o o\\ndodo\\no o o\\no o o\\no o o\\no o o\\no o o\\nodd\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no o\\no\\no\\no\\no\\no\\no\\no o\\no o\\no o\\no o\\no o\\no o\\nO)\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nw\\nX\\no\\nLU\\nLU\\no\\nCO\\nw\\n0)\\nCO\\nto\\nQ)\\n0)\\ncc\\nc\\nCD\\nc 2\\no o\\n\u00e2\u0080\u00a2CT 2\\nIf\\nO 2\\n0\\nTo\\no o\\nw\\no\\nw\\nQ.\\nO\\nCT\\nE\\n5\\nw\\nCO\\nO)\\nk_\\nCT\\nc\\nQ.\\no\\no\\ntr\\nX\\nO\\nCO\\n3\\nQ\\n1\\nU)\\nCO\\n.9\\nii\\nO) 3\\n03\\n03 o\\n5\\n03 3\\nCL\\nc\\no\\nCO\\n\u00e2\u0096\u00a0d\\no\\nQ.\\nCO\\nc\\nCO\\no\\n3\\nCT\\no\\nLU O I-\\nco\\n.3?\\nk_\\no\\nCT\\n0)\\nCO\\no\\nCO\\n3\\no\\n0)\\nc\\nJO\\n0\\nCO\\nr-cvjco ctincoNT-gpoo\\noqqooqoccj^r^o)\\nO)\\nCO\\nk_\\no\\n00\\nCO\\nA\\no\\nJO\\nct\\nCO\\nc\\nco\\nw\\nCT\\nJO\\nQ.\\nw\\nct\\nCO\\no\\nJO\\nQ.\\nc 0\\nE\\no\\nCT\\nA\\nE\\n3\\nc\\nA\\nC\\n3\\no\\nco\\nE\\nCO\\nct\\nc\\nCO\\nk_\\n_cC\\nCD\\nC/5\\nCD\\nk_\\nO\\nCO\\nCD\\n03\\n03\\n-Q\\nCO\\nct\\nct\\nE\\n^_\\nCD\\no\\nA\\nJO\\nCO\\nE\\no\\no\\nCT)\\n3\\nCT\\nc\\nA\\nO\\nc\\no\\n5\\nE\\nCO\\nCD\\n\u00e2\u0096\u00a0o\\nc\\nCO\\n_C0\\nco\\n\u00e2\u0096\u00a0D\\nk_\\n03\\n0\\n_Q\\nO)\\nCO\\nCD\\nO)\\nC\\nCO\\n-C\\no\\n03\\no\\nv_\\nQ.\\nE\\n03\\nO\\nc\\ny)\\n03\\nC\\no\\n03\\n.co\\nE\\n0)\\nCD\\n03\\n03 _\\nIs\\nO C5\\nCO\\nS\\n3\\nm 05\\n.5\\nc\\nE\\nct\\nQ)\\no\\nC 3\\n.9 ffl\\nCO\\no\\n-c\\nQ- o\\n3 5\\n2\\nco\\nCO\\nA\\nco rj\\no\\n0 2\\nco -Q\\n0\\nCT\\nCT\\nCT\\n_3\\no\\nc\\nw\\n_\\nct\\n0 c\\n1\\nCT\\n0 C CT\\nLU h-\\nE\\n7.0 Hazardous Air Pollutants 7-41", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0163.jp2"}, "164": {"fulltext": "Figure 7-1. 1996 NTI State Data Summary\\nNational Air Pollutant Emission Trends, 1990-1998\\n7-42 7.0 Hazardous Air Pollutants\\nGreen states who submitted HAP inventory data\\nX states who submitted revisions by 9/1/99\\nlocal agencies who submitted revisions by 9/1/99", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0164.jp2"}, "165": {"fulltext": "Figure 7-2. U.S. Counties by Urban and Rural Designation\\nNational Air Pollutant Emission Trends, 1990-1998\\nT3\\nU\\nD\\nn\\no\\n4\\no\\nc\\no\\n-o\\nc\\nC/3\\nD\\nC/3\\nO\\n3\\nOh\\nb\\no\\n\u00e2\u0080\u00a2S .y\\n7.0 Hazardous Air Pollutants *7-43", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0165.jp2"}, "166": {"fulltext": "Figure 7-3. Baseline NTI (1990 to 1993)\\nNational Emissions by Urban vs. Rural\\nNational Air Pollutant Emission Trends, 1990-1998\\nC\\nCU\\nn\\n7-44 7.0 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0166.jp2"}, "167": {"fulltext": "Figure 7-4. Baseline NTI (1990 to 1993)\\nNational Emissions of 188 HAPs by Urban vs. Rural\\nNational Air Pollutant Emission Trends, 1990-1998\\n7.0 Hazardous Air Pollutants 7-45\\nTotal urban emissions are 4,330,000 tons Total rural emissions are 1,580,000\\n73% of the total 27% of the total", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0167.jp2"}, "168": {"fulltext": "Figure 7-5. Baseline NTI (1990 to 1993)\\nNational Emissions of 33 HAPs by Urban vs. Rural\\nNational Air Pollutant Emission Trends, 1990-1998\\n7-46 7.0 Hazardous Air Pollutants\\nTotal urban emissions are 943,000 tons Total rural emissions are 480,000 tons\\n66% of the total 34% of the total", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0168.jp2"}, "169": {"fulltext": "Figure 7-6. Baseline NTI (1990 to 1993)\\n188 HAP Emissions By State and Source Sector\\nNational Air Pollutant Emission Trends, 1990-1998\\nO\\n(S\\no\\no\\nc\\nO\\nO\\nO\\ncu\\nCD\\no\\n\u00e2\u0096\u00a0fu\\nn\\nn\\n\u00e2\u0096\u00a1n\\nn\\ninn\\nrnrr\\non\\nl I-\\nerr\\nIIN\\n1\\n\u00e2\u0096\u00a1nn\\nr ii i\\nnr;\\n1 III 1\\nr\\nr JT~\\ni\\n11\\n1-\\nBujuioA/w\\nujSuoosiM\\neiui6.UA }sa/\\\\A\\nuo)6u;ijseM\\nBjUjBjjA\\nf|J IUOLUJ9A\\nsexaj.\\naassauuaj.\\nejo jea mnos\\neujiojeo mnos\\nPUB|S| 9pot(y\\nBjUBAlAsUUdd\\nuoBajo\\nBUJOMB| |0\\n\u00c2\u00b0!MO\\nJ Bio |Ba MIJON\\nBUj|OJBQ MIJON\\n|JOA M3N\\nOOjX 3 M 3 N CO\\nAasjap AA3N Z\\najjMsdujBH M3N\\nBPBA3N\\nB^SBjqaN\\nBUBlUO|/\\\\|\\nunossjiN\\njddjssjssiy\\\\j\\nBiosauuji/y\\nub6;mo!|/\\\\|\\nsnasnMOBSSBiN\\nPUB| AjB|/\\\\| m\\naujB|Ai a\\nBUBjsmoi\\nAipniuay\\nn\\ni\\nCD\\na\\nSBSUB q\\nB ^\u00c2\u00b0i m\\neuBjpui\\nA\\ns\\n-1\\nCD\\nQEC\\nnz\\nmm\\nHE\\nn\\nr ~t\\nr\\nS! \u00c2\u00b0u!\u00e2\u0080\u009ei\\nQMBPI\\n\u00c2\u00abBMBH S*- ,y\\nBjBjoao\\nBpUO|-J CO\\nBjqujn|oo jo puisjQ\\najBMB|aa\\ninojioauuoo\\nOpBJO|OQ\\nBjUJOJj|BQ\\nSBSUB^JV\\nBUOZUV\\nB)|SB|V\\nBLUBqB|V\\nO\\no\\no\\nOJ\\nCO\\nIT)\\nCO\\nCM\\nsuoi pufesnoqj.\\n7.0 Hazardous Air Pollutants -7-47", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0169.jp2"}, "170": {"fulltext": "Figure 7-7. Baseline NTI (1990 to 1993)\\n33 HAP Emissions by State and Source Sector\\nNational Air Pollutant Emission Trends, 1990-1998\\n6u!iuoA/v\\\\\\ninsuoosiM\\nb|U!6j!A }S8/\\\\a\\nuo}6umse/\\\\A\\nB!U|6j!A\\nJU01UJ8A\\nSBX0J_\\n00SS8UU01\\nB}o |Ba mnos\\nBunoJBQ qjnos\\npUB|S| 0pOLjy\\nBjUBAlAsUUOd\\nUO60JO\\nBLUOL|B| jO\\n\u00c2\u00a9NO\\nBJO^BQ PPON\\nBU||OJBO MP\u00c2\u00b0N\\n)JOA M0N\\nOOjXOAl M8N\\nAoSJOf M0|s|\\n0J|LjSdUJBH M0|\\\\|\\nBpBA8|S|\\nB )SBJq8N\\nBUB}U01/\\\\|\\njjnossjiAJ\\njddjSSjssjiAl\\nB1OS0UUI1AI\\nUB6jqo!AI\\nsu8snqoBSSBi/\\\\|\\nPUB|AJB[A|\\n8U|B|AI\\nBUBjSmcn\\nA )onju0 i\\nSBSUB\u00c2\u00bb\\nB/V\\\\0|\\nBUBipU|\\nSjOUjlll\\noqepi\\nIjBAABH\\nb|6jo89\\nBp|JO| J\\nBiqainioQ jo lojjjsia\\n8JBMB|0Q\\ninojpouuoQ\\n0PBJ0|00\\nBjUJOjjlBQ\\nSBSUB (JV\\nBUOZUV\\ne |SB|v\\nBUJBqBIV\\nO\\nLO\\nO\\no\\no\\nin\\no\\nsuoj_ puesnoLji\\n7.0 Hazardous Air Pollutants 7-48", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0170.jp2"}, "171": {"fulltext": "Figure 7-8. Summed Baseline NTI (1990 to 1993) Emissions of 188\\nHAPS per Square Mile for U.S. Counties\\nNational Air Pollutant Emission Trends, 1990-1998\\n7.0 Hazardous Air Pollutants 7-49", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0171.jp2"}, "172": {"fulltext": "National Air Pollutant Emission Trends, 1990-1998\\nta-wH Wn\\nT]\\ntrftfrPW\\nr\\nJ\\n4_XuIP-JI L\\n-A 7 r J 1 1 j 1 1_\\nl\\n0\\nL-\\nP\\nr\\n7-50 7.0 Hazardous Air Pollutants", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0172.jp2"}, "173": {"fulltext": "Figure 7-10. Summary of Baseline NTI (1990 to 1993) of 33 HAPs\\nNational Emissions Percentage by Source Sector\\nNational Air Pollutant Emission Trends, 1990-1998\\nO\\n03\\nO\\n\u00e2\u0080\u009cO\\n03\\nO\\nO\\napuoiqo |Au|a\\nauaiAqjaojoiqoui\\naua|AmaojO|qoej}ai\\naujioumo\\napuoiLjOjp aua|Adojd\\n(HVd-91. se) lAlOd\\nS|Auaqd(q pa}Buuo|q3A|Od\\nspunodiuoo |a |0!N\\napuoiqo aua|Aq}ay\\\\|\\nspunodoioQ AjnojaiAi\\nspunodiuoo asaue6uB^\\\\|\\nspunodiuoo pBa~|\\naujZBjpAn\\nauazuaqojoiqoBxan\\napAqap|BLUJOd\\napixo aua|Aqj 3\\napuoiqojp aua|Aqjg\\napiujojqip aua|Aq}g\\nSUOjSSIlUg U3A0 a^jOQ\\nspunodiuoo LunjLuojqo\\nujjopjoiqo\\napMO|qoBj;a} uoqjBQ\\nspunodiuoo ainiujpBO\\nspunodiuoo iuni||Ajag\\nauazuag\\nspunodiuoo ojuasjy\\na|U}iuo|Ajov\\nujaiojoy\\napAqap|B}aoy\\nD 3 i aaoi-8\u00e2\u0080\u0098z\u00e2\u0080\u0098e\u00e2\u0080\u00982\\nauadojdojO|qoia-e\u00e2\u0080\u0098 l\\naua!pB}ng-e\u00e2\u0080\u0098i.\\nauBq)aojo|qoBJ}ai-2\u00e2\u0080\u00982\u00e2\u0080\u0098 j.\\nOoOOOOOOOOo\\nOcDOOr^CDLO^COCNT-\\n7.0 Hazardous Air Pollutants 7-51", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0173.jp2"}, "174": {"fulltext": "[This page intentionally left blank.]", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0174.jp2"}, "175": {"fulltext": "Chapter 8.0 National Greenhouse Gas\\nEmissions\\n8.1 WHAT INFORMATION IS PRESENTED\\nIN THIS CHAPTER?\\nThis chapter summarizes the latest information on\\nanthropogenic greenhouse gas emissions in the United States\\nfrom 1990 through 1997. For a more detailed discussion, the\\nreader is referred to the Inventory of U.S. Greenhouse Gas\\nEmissions and Sinks: 1990-1991 April 1999, United States\\n(U.S.) Environmental Protection Agency (EPA), EPA 236-R-\\n99-003. This report is produced annually and submitted by the\\nU.S. Government to the United Nations as part of our\\ncommitments under the Framework Convention on Climate\\nChange (UNFCCC). Readers interested in the international\\nefforts to address the problem of climate change through\\nnegotiation are referred to the home page of the UNFCCC at\\nhttp://www.unfccc.de. Readers interested in more\\nbackground on the science of climate change, global warming\\nor greenhouse gases are referred to the Intergovernmental\\nPanel on Climate Change (IPCC) via their website at\\nhttp://www.ipcc.ch.\\nTo ensure that the U.S. greenhouse gas emissions\\ninventory meets the reporting requirements of the UNFCCC,\\nthe estimates were calculated using methodologies consistent\\nwith those recommended in the Revised 1996 IPCC Guidelines\\nfor National Greenhouse Gas Inventories 1 For most source\\ncategories the IPCC default methodologies were expanded in\\norder to incorporate emission factors and data specific to the\\nUnited States, resulting in a more comprehensive and detailed\\nestimate of U.S. emissions. (See Section 8.3.3.)\\n8.2 WHAT ARE THE RECENT TRENDS IN\\nU.S. GREENHOUSE GAS EMISSIONS?\\nNaturally occurring greenhouse gases include water\\nvapor, carbon dioxide (C0 2 methane (CH 4 nitrous oxide\\n(N 2 0), and ozone (0 3 Several classes of halogenated\\nsubstances that contain fluorine, chlorine, or bromine are also\\ngreenhouse gases, but they are, for the most part, solely a\\nproduct of industrial activities. Chlorofluorocarbons (CFCs)\\nand hydrochlorofluorocarbons (HCFCs) are halocarbons that\\ncontain chlorine, while halocarbons that contain bromine are\\nreferred to as halons. Other fluorine containing halogenated\\nsubstances include hydrofluorocarbons (HFCs),\\nperfluorocarbons (PFCs), and sulfur hexafluoride (SF 6\\nTotal U.S. greenhouse gas emissions rose in 1997 to\\n1,813.6 million metric tons of carbon equivalents (MMTCE).\\nThe single year increase in emissions from 1996 to 1997 was\\n1.3 percent (23.1 MMTCE), down from the previous year\u00e2\u0080\u0099s\\nincrease of 3.3 percent. Overall, emissions of greenhouse\\ngases have increased 11 percent above 1990 levels. Table 8-1\\nprovides a detailed summary of U.S. greenhouse gas emissions\\nand sinks for 1990 through 1997.\\nIn 1997, the primary greenhouse gas emitted by human\\nactivities was C0 2 The largest source of C0 2 and of overall\\ngreenhouse gas emissions in the United States was fossil fuel\\ncombustion. CH 4 emissions resulted primarily from\\ndecomposition of wastes in landfills, manure and enteric\\nfermentation associated with domestic livestock, natural gas\\nsystems, and coal mining. Emissions of N 2 0 were dominated\\nby agricultural soil management and mobile source fossil fuel\\ncombustion. The substitution of 0 3 depleting substances and\\nemissions of HFC-23 during the production of HCFC-22 were\\nthe primary contributors to aggregate HFC emissions. PFC\\nemissions came mainly from primary aluminum production,\\nwhile electrical transmission and distribution systems emitted\\nthe majority of SF 6\\nAs the largest source of U.S. greenhouse gas emissions,\\nC0 2 from fossil fuel combustion accounted for 81 percent of\\nemissions in 1997 when each gas is weighted by its Global\\nWarming Potential (see Figure 8-1 in the Inventory of U.S.\\nGreenhouse Gas Emissions and Sinks: 1900-1997 for a\\ndiscussion of global warming potentials). Emissions from\\nfossil fuel combustion grew by 11 percent (138.8 MMTCE)\\nover the 8-year period and were responsible for over three-\\nquarters of the increase in national emissions. The annual\\nincrease in C0 2 emissions from this source was 1.3 percent in\\n1997, down from the previous year when emissions increased\\nby 3.6 percent.\\nThe dramatic increase in fossil fuel combustion related\\nC0 2 emissions in 1996 was primarily a function of two\\nfactors: 1) fuel switching by electric utilities from natural gas\\nto more carbon intensive coal as gas prices rose sharply due to\\nweather conditions, which drove up residential consumption\\nof natural gas for heating; and 2) higher petroleum\\nconsumption for transportation. In 1997, by comparison.\\n8.0 National Greenhouse Gas Emissions 8-1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0175.jp2"}, "176": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nelectric utility natural gas consumption rose to regain much of\\nthe previous year\u00e2\u0080\u0099s decline as the supply available rose due to\\nlower residential consumption. Despite this increase in natural\\ngas consumption by utilities and relatively stagnant U.S.\\nelectricity consumption, coal consumption rose in 1997 to\\noffset the temporary shut-down of several nuclear power\\nplants. Petroleum consumption for transportation activities in\\n1997 also grew by less than a percent, compared to almost 4\\npercent the previous year (see Table 8-2).\\nOverall, from 1990 to 1997, total emissions of C0 2 CH 4\\nand N 2 0 increased by 143.5 (11 percent), 9.7 (6 percent), and\\n13.4 MMTCE (14 percent), respectively. During the same\\nperiod, weighted emissions of HFCs, PFCs, and SF 6 rose by\\n14.9 MMTCE (67 percent). Despite being emitted in smaller\\nquantities, emissions of HFCs, PFCs, and SF 6 are significant\\nbecause of their extremely high global warming potentials and,\\nin the cases of PFCs and SF 6 long atmospheric lifetimes.\\nConversely, U.S. greenhouse gas emissions were partly offset\\nby carbon sequestration in forests, which was estimated to be\\n11 percent of total emissions.\\nOther significant trends in emissions from other source\\ncategories over the 8-year period of 1990 through 1997\\nincluded:\\nAggregate HFC and PFC emissions resulting from\\nthe substitution of ozone depleting substances (e.g.,\\nCFCs) increased dramatically (by 14.4 MMTCE).\\nThis increase was partly offset, however, by\\nreductions in PFC emissions from aluminum\\nproduction (41 percent) and HFC emissions from\\nHCFC-22 production (14 percent), both as a result of\\nvoluntary industry emission reduction efforts and, in\\nthe former case, from falling domestic aluminum\\nproduction.\\nCombined N,0 and CH 4 emissions from mobile\\nsource fossil fuel combustion rose 3.9 MMTCE (26\\npercent), primarily due to increased rates of N 2 0\\ngeneration in highway vehicles.\\nCH 4 emissions from the decomposition of waste in\\nmunicipal and industrial landfills rose by 10.5\\nMMTCE (19 percent) as the amount of organic\\nmatter in landfills steadily accumulated.\\nEmissions from coal mining dropped by 5.2 MMTCE\\n(21 percent) as the use of CH 4 from degasification\\nsystems increased significantly.\\nN 2 0 emissions from agricultural soil management\\nincreased by 8.8 MMTCE (13 percent) as fertilizer\\nconsumption and cultivation of nitrogen fixing crops\\nrose.\\nAn additional domestic adipic acid plant installed\\nemission control systems in 1997, which was\\nestimated to have resulted in a 1.4 MMTCE (27\\npercent) decline in emissions from 1996 to 1997\\ndespite an increase in production.\\n8.3 WAS A MORE DETAILED ANALYSIS\\nOF INDUSTRIAL EMISSIONS\\nCONDUCTED?\\nYes. An analysis of the industrial sector was conducted\\nto provide greater resolution on the greenhouse gas emissions\\nand energy consumption trends in the industrial end-use\\nsector.\\nFigures 8-1 through 8-3 present C0 2 emissions data by\\nindustry end-use sector for the entire United States in the year\\n1994.\\n8.3.1 What Data Were Used in this Analysis?\\nThis analysis was based on data contained in several EPA\\nand Energy Information Administration (EIA) reports: the\\nManufacturing Consumption of Energy 1994, DOE/EIA-\\n0512(94); 2 The Annual Energy Review 1997, DOE/EIA-\\n0384(97); 3 Emissions of Greenhouse Gases in the United\\nStates 1997, DOE/EIA-0573(97); 4 and the Inventory of U.S.\\nGreenhouse Gas Emissions and Sinks: 1990-1996, EPA 236-\\nR-98-006. 5\\nThe Annual Energy Review, EIA and the Emissions of\\nGreenhouse Gases, EPA were used to develop national\\nestimates of C0 2 for the year 1994. Both of these inventories\\nreport data on C0 2 emissions caused by both fuel combustion\\nand industrial processes, and both were included in this\\nanalysis. Typically, fossil fuel combustion represents 81\\npercent of total U.S. greenhouse gas emissions and 99 percent\\nof total U.S. C0 2 emissions, although there is some year-to-\\nyear variance. Cement manufacture is the largest remaining\\nsource of industrial C0 2 emissions, and has been estimated to\\ncontribute about 10 MMTCE to annual U.S. emissions. For\\nmore information on industrial sources of C0 2 or other\\ngreenhouse gas emission data, the reader is referred to the\\nEPA inventory document or web site at www.epa.gov/\\nglobalwarming/inventory.\\nThe Manufacturing Consumption of Energy (MECS) data\\nwere used to develop the detailed estimates for the industry\\nsector. The MECS data are prepared once every 4 years, thus\\n1994 is presented as the most recent year for which the MECS\\ndata are available. The MECS data contain rich detail on\\nmanufacturing industries, but no information on the non\u00c2\u00ac\\nmanufacturing industries, such as agricultural activity, mining,\\nand construction. The MECS data were merged with estimates\\nof total industrial energy use to develop these results. Emission\\nestimates were developed using carbon coefficients for various\\nfuel types, and for a quality assurance check, were compared\\n8-2 8.0 National Greenhouse Gas Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0176.jp2"}, "177": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nwith national inventory data. Refer to Annex A of the EPA\\nInventory document for more detail on carbon coefficients for\\nfuel types. Table 8-3 presents the actual carbon coefficients\\nused in this analysis.\\n8.3.2 What are the Results?\\nThe results of this analysis show that the majority of CO,\\nemissions can be attributed to a few major end-use sectors.\\nThe utility sector, which represents 36 percent of total\\nCO, emissions in 1994, supplies energy to industry.\\nEmissions resulting from electricity production can thus be\\nprorated to industry on the basis of electricity consumption.\\nIdeally, this would be done on a regional basis in order to best\\ncapture the complexity of our nation\u00e2\u0080\u0099s energy supply system\\nand to account for variations in carbon emissions per kilowatt\\nhour. However, this analysis uses national averages to develop\\nthe carbon emissions embedded in electricity consumption and\\nattributes these emissions to the industries on the basis of their\\nelectricity demand.\\nFigure 8.1 shows total U.S. CO, emissions in 1994.\\nUtilities contribute 36 percent of that total, with transportation\\nthe second largest sector at 30 percent of total CO, emissions.\\nEmissions from utilities were estimated at 492 MMTCE in\\n1994, with 87 percent of that total resulting from coal\\nconsumption, 9 percent from natural gas, and 4 percent from\\npetroleum fuel consumption.\\nFigure 8.2 presents all industrial emissions of C0 2 both\\nmanufacturing and non-manufacturing and the graph was\\ndeveloped to account for both \u00e2\u0080\u009con-site\u00e2\u0080\u009d and \u00e2\u0080\u009coff-site\u00e2\u0080\u009d\\nemissions. In this case, on-site emissions are process-related\\nemissions such as CO, flux from lime calcination, and off-site\\nemissions refer to the emissions that result from fossil fuel\\nconsumption at power plants supplying electricity to industry.\\nFigure 8.3 presents C0 2 emissions for the entire United\\nStates, and differs from Figure 8.1 in that utility sector has\\nbeen \u00e2\u0080\u009cmapped\u00e2\u0080\u009d into the various end-use sectors that consume\\nthe electricity generated at utilities. Table 8.4 presents the C0 2\\nemissions data in tabular form.\\n8.3.3 What Methodologies were Utilized?\\nEmissions of greenhouse gases from various sources have\\nbeen estimated using methodologies that are consistent with\\nthe Revised 19961PCC Guidelines for National Greenhouse\\nGas Inventories To the extent possible, the present U.S.\\ninventory relies on published activity and emission factor data.\\nDepending on the emission source category, activity data can\\ninclude fuel consumption or deliveries, vehicle-miles traveled,\\nraw material processed, etc.; emission factors are factors that\\nrelate quantities of emissions to an activity. For some sources,\\nIPCC default methodologies and emission factors have been\\nemployed. However, for emission sources considered to be\\nsignificant sources in the United States, the IPCC default\\nmethodologies were expanded and more comprehensive\\nmethods were applied. The Annexes of the Inventory of U.S.\\nGreenhouse Gas Emissions and Sinks: 1990-1997 contain\\nadditional detail and documentation on the calculations and\\nassumptions used to obtain these estimates. This report can be\\nfound online at vvvvw.epa.gov/globalwarming/inventory.\\nInventory emission estimates from energy consumption\\nand production activities are based primarily on the latest\\nofficial fuel consumption data from the EIA/DOE. C0 2\\nemissions from fuel combusted in ships or aircraft engaged in\\nthe international transport of passengers or cargo are not\\nincluded in U.S. totals, but are reported separately as\\ninternational bunkers in accordance with IPCC reporting\\nguidelines. 1 CO, emissions from fuel combusted within U.S.\\nterritories, however, are included in U.S. totals.\\nData on fuel consumption for the United States and its\\nterritories, carbon content of fuels, and percent of carbon\\nsequestered in non-energy uses were obtained directly from\\nthe EIA/DOE. Fuel consumption data were obtained primarily\\nfrom the Monthly Energy Review 6 and various EIA databases.\\nU.S. marine bunker fuel consumption data for distillate and\\nresidual fuel oil was taken from Fuel Oil and Kerosene Sales. 1\\nMarine bunker fuel consumption in U.S. territories was\\ncollected from internal EIA databases 8 used to prepare the\\nInternational Energy Annual 9 Jet fuel consumption for\\naviation international bunkers was taken from Fuel Cost and\\nConsumption 10 which are monthly data releases by the\\nDepartment of Transportation\u00e2\u0080\u0099s Bureau of Transportation\\nStatistics (DOT/BTS), and unpublished data from the Bureau\\nof Economic Analysis (BEA). 11 The data collected by\\nDOT/BTS includes fuel consumed for international\\ncommercial flights both originating and terminating in the\\nUnited States. One-half of this value was assumed to have\\nbeen purchased in the United States/ 1\\nIPCC 1 provided combustion efficiency rates for petroleum\\nand natural gas. Bechtel provided the combustion efficiency\\nrates for coal. Vehicle type fuel consumption data for the\\nallocation of transportation sector emissions were primarily\\ntaken from the Transportation Energy Databook 12 prepared by\\nthe Center for Transportation Analysis at Oak Ridge National\\nLaboratory (DOE 1993, 1994, 1995, 1996, 1997, 1998). All\\njet fuel and aviation gasoline were assumed to have been\\nconsumed in aircraft.\\n8.0 National Greenhouse Gas Emissions 8-3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0177.jp2"}, "178": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\n8.4 REFERENCES\\n1. \u00e2\u0080\u009cRevised 1996 IPCC Guidelines for National Greenhouse Gas Inventories,\u00e2\u0080\u009d Paris: Intergovernmental Panel on Climate\\nChange, United Nations Environment Programme, Organization for Economic Co-Operation and Development,\\nInternational Energy Agency. 1997.\\n2. \u00e2\u0080\u009cManufacturing Consumption of Energy 1994,\u00e2\u0080\u009d DOE/EIA-0512(94), Energy Information Administration, U.S.\\nDepartment of Energy, Washingotn, DC. 1994.\\n3. \u00e2\u0080\u009cAnnual Energy Review 1997,\u00e2\u0080\u009d DOE/EIA- 0384(97)-annual, Energy Information Administration, U.S. Department of\\nEnergy, Washington, DC. July 1998.\\n4. \u00e2\u0080\u009cEmissions of Greenhouse Gases in the United States 1997,\u00e2\u0080\u009d DOE/EIA-0573(97), Energy Information Administration,\\nU.S. Department of Energy, Washington, DC. 1997.\\n5. \u00e2\u0080\u009cInventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-1997,\u00e2\u0080\u009d EPA 236-R-99-003, U.S. Environmental\\nProtection Agency. April 1999.\\n6. \u00e2\u0080\u009cMonthly Energy Review,\u00e2\u0080\u009d DOE/EIA- 0035(98)-monthly, Energy Information Administration, U.S. Department of\\nEnergy, Washington, DC. July 1998.\\n7. \u00e2\u0080\u009cFuel Oil and Kerosene Sales 1997,\u00e2\u0080\u009d DOE/EIA-0535(97)-annual, Energy Information Administration, U.S. Department\\nof Energy, Washington, DC. 1998.\\n8. \u00e2\u0080\u009cReport of Bunker Fuel Oil Laden on Vessels Cleared for Foreign Countries,\u00e2\u0080\u009d unpublished, Form-563, Foreign Trade\\nDivision, Bureau of the Census, U.S. Department of Commerce. 1998.\\n9. \u00e2\u0080\u009cInternational Energy Annual 1996,\u00e2\u0080\u009d DOE/EIA-0219(96)-annual, Energy Information Administration, U.S. Department\\nof Energy, Washington, DC. 1998.\\n10. \u00e2\u0080\u009cFuel Cost and Consumption,\u00e2\u0080\u009d monthly reports, DAI-10, Federal Aviation Administration, U.S. BTS, Department of\\nTransportation, Washington, DC. 1998.\\n11. \u00e2\u0080\u009cSurvey of Current Business,\u00e2\u0080\u009d Bureau of Economic Analysis, Department of Commerce, Table 2A, p. 152, August 1998.\\nhttp://www.bea.doc.gov/bea.dnl.htm\\n12. DOE (1993-1998) \u00e2\u0080\u009cTransportation Energy Databook,\u00e2\u0080\u009d (1993-1998), prepared by the Center for Transportation Analysis\\nat Oak Ridge National Laboratory for the Department of Energy, Oak Ridge, IL.\\nd. See section titled International Bunker Fuels for a more detailed discussion.\\n8-4 8.0 National Greenhouse Gas Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0178.jp2"}, "179": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 8-1. Recent Trends In U.S. Greenhouse Gas Emissions and Sinks (MMTCE)\\nGas/Source\\n1990\\n1991\\n1992\\n1993\\n1994\\n1995\\n1996\\n1997\\nCM\\nO\\no\\n1,344.3\\n1,329.8\\n1,349.6\\n1,379.2\\n1,403.5\\n1,419.2\\n1,469.3\\n1,487.9\\nFossil Fuel Combustion\\n1,327.2\\n1,312.6\\n1,332.4\\n1,360.6\\n1,383.9\\n1,397.8\\n1,447.7\\n1,466.0\\nNatural Gas Flaring\\n2.3\\n2.6\\n2.6\\n3.5\\n3.6\\n4.5\\n4.3\\n4.2\\nCement Manufacture\\n8.9\\n8.7\\n8.8\\n9.3\\n9.6\\n9.9\\n9.9\\n10.2\\nLime Manufacture\\n3.3\\n3.2\\n3.3\\n3.4\\n3.5\\n3.7\\n3.8\\n3.9\\nLimestone and Dolomite Use\\n1.4\\n1.3\\n1.2\\n1.1\\n1.5\\n1.9\\n2.0\\n2.1\\nSoda Ash Manufacture and Consumption\\n1.1\\n1.1\\n1.1\\n1.1\\n1.1\\n1.2\\n1.2\\n1.2\\nCarbon Dioxide Consumption\\n0.2\\n0.2\\n0.2\\n0.2\\n0.2\\n0.3\\n0.3\\n0.3\\nLand-Use Change and Forestry (Sink) 3\\n(311.5)\\n(311.5)\\n(311.5)\\n(208.6)\\n(208.6)\\n(208.6)\\n(208.6)\\n(208.6)\\nInternational Bunker Fuels 13\\n27.1\\n27.8\\n29.0\\n29.9\\n27.4\\n25.4\\n25.4\\n26.6\\nch 4\\n169.9\\n171.0\\n172.5\\n172.0\\n175.5\\n178.6\\n178.3\\n179.6\\nStationary Sources\\n2.3\\n2.4\\n2.4\\n2.4\\n2.4\\n2.5\\n2.5\\n2.2\\nMobile Sources\\n1.4\\n1.4\\n1.4\\n1.4\\n1.4\\n1.4\\n1.4\\n1.4\\nCoal Mining\\n24.0\\n22.8\\n22.0\\n19.2\\n19.4\\n20.3\\n18.9\\n18.8\\nNatural Gas Systems\\n32.9\\n33.3\\n33.9\\n34.1\\n33.5\\n33.2\\n33.7\\n33.5\\nPetroleum Systems\\n1.6\\n1.6\\n1.6\\n1.6\\n1.6\\n1.6\\n1.5\\n1.6\\nPetrochemical Production\\n0.3\\n0.3\\n0.3\\n0.4\\n0.4\\n0.4\\n0.4\\n0.4\\nSilicon Carbide Production\\nEnteric Fermentation\\n32.7\\n32.8\\n33.2\\n33.6\\n34.5\\n34.9\\n34.5\\n34.1\\nManure Management\\n14.9\\n15.4\\n16.0\\n16.1\\n16.7\\n16.9\\n16.6\\n17.0\\nRice Cultivation\\n2.5\\n2.5\\n2.8\\n2.5\\n3.0\\n2.8\\n2.5\\n2.7\\nAgricultural Residue Burning\\n0.2\\n0.2\\n0.2\\n0.2\\n0.2\\n0.2\\n0.2\\n0.2\\nLandfills\\n56.2\\n57.6\\n57.8\\n59.7\\n61.6\\n63.6\\n65.1\\n66.7\\nWastewater Treatment\\n0.9\\n0.9\\n0.9\\n0.9\\n0.9\\n0.9\\n0.9\\n0.9\\nInternational Bunker Fuels 13\\nN 2 0\\n95.7\\n97.6\\n100.1\\n100.4\\n108.3\\n105.4\\n108.2\\n109.0\\nStationary Sources\\n3.8\\n3.8\\n3.9\\n3.9\\n4.0\\n4.0\\n4.1\\n4.1\\nMobile Sources\\n13.6\\n14.2\\n15.2\\n15.9\\n16.7\\n17.0\\n17.4\\n17.5\\nAdipic Acid\\n4.7\\n4.9\\n4.6\\n4.9\\n5.2\\n5.2\\n5.4\\n3.9\\nNitric Acid\\n3.3\\n3.3\\n3.4\\n3.5\\n3.7\\n3.7\\n3.9\\n3.8\\nManure Management\\n2.6\\n2.8\\n2.8\\n2.9\\n2.9\\n2.9\\n3.0\\n3.0\\nAgricultural Soil Management\\n65.3\\n66.2\\n68.0\\n67.0\\n73.4\\n70.2\\n72.0\\n74.1\\nAgricultural Residue Burning\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\nFluman Sewage\\n2.1\\n2.1\\n2.2\\n2.2\\n2.2\\n2.3\\n2.3\\n2.3\\nWaste Combustion\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\n0.1\\nInternational Bunker Fuels 3\\n0.2\\n0.2\\n0.2\\n0.3\\n0.2\\n0.2\\n0.2\\n0.2\\nHFCs, PFCs, and SF 6\\n22.2\\n21.6\\n23.0\\n23.4\\n25.9\\n30.8\\n34.7\\n37.1\\nSubstitution of Ozone Depleting Substances\\n0.3\\n0.2\\n0.4\\n1.4\\n4.0\\n9.5\\n11.9\\n14.7\\nAluminum Production\\n4.9\\n4.7\\n4.1\\n3.5\\n2.8\\n2.7\\n2.9\\n2.9\\nHCFC-22 Production\\n9.5\\n8.4\\n9.5\\n8.7\\n8.6\\n7.4\\n8.5\\n8.2\\nSemiconductor Manufacture\\n0.2\\n0.4\\n0.6\\n0.8\\n1.0\\n1.2\\n1.4\\n1.3\\nElectrical Transmission and Distribution\\n5.6\\n5.9\\n6.2\\n6.4\\n6.7\\n7.0\\n7.0\\n7.0\\nMagnesium Production and Processing\\n1.7\\n2.0\\n2.2\\n2.5\\n2.7\\n3.0\\n3.0\\n3.0\\nTotal Emissions\\n1,632.1\\n1,620.0\\n1,645.2\\n1,675.0\\n1,713.2\\n1,733.9\\n1,790.5\\n1,813.6\\nNet Emissions (Sources and Sinks)\\n1,320.6\\n1,308.5\\n1,333.7\\n1,466.5\\n1,504.7\\n1,525.4\\n1,582.0\\n1,605.0\\nDoes not exceed 0.05 MMTCE\\na Sinks are only included in net emissions total. Estimates of net carbon sequestration due to land-use change and forestry activities exclude\\nnon-forest soils, and are based partially upon projections of forest carbon stocks.\\nb Emissions from International Bunker Fuels are not included in totals.\\nNote: Totals may not sum due to independent rounding.\\n8.0 National Greenhouse Gas Emissions 8-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0179.jp2"}, "180": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 8-2. Annual Percent Change in C0 2 Emissions from Fossil Fuel\\nCombustion for Selected Sectors and Fuels\\nSector\\nFuel Type\\n1995 to 1996\\n1996 to 1997\\nElectric Utility\\nCoal\\n5.7%\\n2.9%\\nElectric Utility\\nNatural Gas\\n-14.6%\\n8.7%\\nResidential\\nNatural Gas\\n8.1%\\n-4.4%\\nTransportation*\\nPetroleum\\n3.4%\\n0.3%\\nExcludes emissions from International Bunker Fuels\\nTable 8-3. Carbon Coefficients, MMTCE/QBtu (Q=E15)\\nYear\\nElectricity\\nResidual Oil\\nDistillate Oil\\nNG\\nLPG\\nCoal\\nCoke\\nStill Gas\\n1994\\n50\\n21.49\\n19.95\\n14\\n17.01\\n25\\n25\\n20.19\\n1995\\n50\\n21.49\\n19.95\\n14\\n16.99\\n25\\n25\\n20.23\\n8-6 8.0 National Greenhouse Gas Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0180.jp2"}, "181": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nHI\\no\\na\\nJ\\nif)\\n0\\nC\\no\\n\u00e2\u0080\u0098(f)\\n(D\\nMM\\nE\\nLU\\n0\\n~o\\nrnwmm\\nX\\no\\nb\\nc\\no\\nA\\ni\u00e2\u0080\u0094\\n0\\no\\nI\\noo\\n0\\nA\\n0\\n0\\n3\\nO\\n3\\nw\\nE 0\\nC U\\n0\\n0\\nE\\nLU\\nro\\nc\\n-.2\\no\\nt\u00e2\u0080\u0094 O w\\n0.2\\nw\\nsO\\no\\nE\\nLU\\n0\\n2\\nC\\no\\nCM\\nc n O\\nc/5\\nc\\nCO\\nE\\nLU\\nE\\no\\nq\\nw\\nw\\n0 0\\no O\\no o\\n0\\nO r\\noi\\no o\\n0\\no\\nO\\nO\\nE\\n3\\n0\\no\\nk_\\n0\\nCL\\nH\\no\\no\\n_0\\nLU\\nO\\nOl|\\n0\\nCD\\no\\n0\\no\\n_\\n3\\nO\\no\\n0\\nx\u00c2\u00b0 vO sP vP vO vO\\nO CP 1 0 s O ft s\\nT- LO CM O T-\\n\\\\0 \\\\0 vO \\\\0 \\\\0 \\\\u\\nO O O O o qS qS fys\\nO O O CM O 0 0\\nP P xO ^0 -^0 ^C)\\no o o o o o o\\nO CM M- t- O O\\np vP xO xO\\nO O O\\nT- O O\\nxp xO xP xP\\nO O O O\\nCO lO CM (D\\nC\\\\J CM 1- T-\\nO O O\\no o o\\nCM CD CM\\nxp\\no\\nO\\nx 0 xO\\nO o\\nT- O\\no o\\nO O\\nP xP xP Xp xP\\nO 0 s 0 s O o\\nCM CD LO LO t-\\nxP P P\\no o o\\nO 00 LO\\nxP xP xP\\nO O O\\nP xp\\nO o\\nO O\\nxO x^O xO X.O\\no 0 s- 0 s o sy\\nLO O LO CT\\nCO 00 T- T-\\nxP\\no\\nLO\\nP\\no\\nCO\\nLO O\\nxP\\no\\nCM\\nx P P\\no o o\\nO t- O\\nxV xV\\nO o\\nCD t-\\no O x\\nio in o\\nif: c\\\\j o\\n\\\\y\\no\\nxs$ vP xP\\no O 0 s o\\nCM CM C\\\\J C\\\\J\\nv0\\nxO\\no CM\\nO O\\noqr^qcoocMcooocoojT-o\\nodcModd-r^oddco-r^dd\\nN ID O\\n^1-0 0 0 0 0 0\\nCM\\no^r- -qooqT-qq^rq- -qcqqqqqr -qqT^q\\ndd^d-r-ddddddddddddddddddd\\nCM\\no\\no\\no q\\nd LO\\nct rx\\nc\\no\\no\\n3\\nk.\\n0\\nc\\no\\no\\n\u00c2\u00b03\\n0\\no\\n3\\n0\\no\\n0\\no\\nm Q-\\n3\\no\\nL\\nCP\\nCP\\nc 0\\nI\\nCf)\\no\\nCL O\\nO Q.\\n8 0\\nCD\\n-Q X\\no q\\n0\\no\\n0\\n0\\nk_\\n3\\nO\\n\u00c2\u00b0a\\nCP\\nc\\nd\\n*0\\nQC\\nE\\nI- I- -I\\n0\\nk_\\n03\\nk_\\n0\\n-0\\niV\\nk_\\nD\\nCP\\n1 c\\n0\\ncu\\no 8\\nE o\\nk_\\n0\\nJD\\nk.\\n0\\n0\\nQ_\\nE\\nC\\nk.\\nQ. C\\n0 i:\\nJD\\nffl\\nQ_\\nU\\nD\\n0 C\\n0\\n3\\n0\\n_l\\nLL\\n0. CL\\nO CL\\nQC\\n0\\n0\\n_0\\no _\\nofl 5\\n2\\nE\\n7a\\nCD .2\\n\u00c2\u00a7.i|\\nCD\\nCO CL LL\\n0\\n0\\nE\\n\u00e2\u0096\u00a00\\nQ_\\nCP\\n0\\nc\\nd\\no\\nQ.\\nd\\n_\\nct\\n0\\nC\\nc\\n1 _\\n3\\no\\n0\\ncr\\no\\nE\\n0\\n0 r;\\nd\\n0\\ng\\nd\\n0 C\\no\\nc\\n0\\nM\\no\\nCL E\\nE\\nCO\\nk_\\n0 3\\no\\nw\\n3\\n0\\no\\n0\\nC\\nw\\nC\\nLU\\nh= -E\\n2\\nxP\\nO\\nCM\\nCO\\nxp\\no o\\no O\\nO O\\nCD\\nI x\\nCD\\nCM\\nt-;\\n\u00c2\u00b09\\nO)\\n\u00c2\u00b09\\nrx-\\n00\\nCO\\nco\\nLO\\nCM\\nco\\nco\\nLO\\nCD\\n00\\n0\\nq\\nq\\nCM\\ni\u00e2\u0080\u0094\\nT~\\nq\\no\\nLO\\nCO\\nco\\nd\\no\\nd\\n\u00e2\u0080\u00a2t\u00e2\u0080\u0094\\nLO\\nq\\no\\nod\\ncd\\ncd\\nd\\no\\ni\\nd\\nK\\no\\nd\\ny-J\\nd\\nCM\\nd\\nd\\no\\no\\nCM\\nCO\\nCM\\nCO\\nrs\\nI x\\nco\\nCD\\ni\u00e2\u0080\u0094\\nCO\\nCM\\ni\u00e2\u0080\u0094\\nCD\\n3\\n0\\nCM\\nCM\\nT_\\nO\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nO\\no\\no\\nO\\nO\\no\\no\\no\\no\\no\\nd\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\no\\nCD\\no\\no\\no\\no\\no\\no\\no\\nd\\no\\nd\\no\\no\\nd\\no^oo^roooo^r\\nco o o o o\\nCO\\nTf o\\nt\u00e2\u0080\u009c o\\nco\\no\\nq\\nco\\nrx\\nco\\no\\nrx\\n0\\no\\nq\\no\\no\\nCM\\nq\\nCM\\ny-\\no\\nco\\nCO\\nCM\\nq\\n\u00c2\u00b09\\no\\nCM\\nd\\no\\nT\u00e2\u0080\u009c\\nd\\no\\no\\nd\\no\\nd\\no\\nq\\no\\nd\\nq\\nd\\nq\\nq\\nc\\\\i\\no\\no\\nd\\no\\nCM\\nq\\no\\nd\\nCM\\ni\u00e2\u0080\u0094\\nCM\\n1\u00e2\u0080\u0094\\n0\\nrx\\nLO\\nCM\\no\\n0\\no\\no\\nq\\no\\nq\\nrx\\nco\\no\\nfx.\\nCM\\nCM\\no\\nq\\nq\\nco\\no\\no\\nd\\no\\no\\no\\no\\nd\\no\\nq\\nCM\\no\\no\\no\\nq\\no\\no\\no\\no\\no\\no\\nd\\nq\\nd\\nd\\no\\nd\\ni\u00e2\u0080\u0094\\ni\u00e2\u0080\u0094\\nCM\\no\\n0\\nLO\\nq\\nCM\\nCD\\nco\\nq\\no\\nCM\\nLO\\nCM\\nCM\\nCO\\nCO\\nIO\\nrx\\nCD\\nq\\no\\nq\\no\\nO\\no\\no\\nq\\nd\\no\\nd\\nyj\\nd\\nq\\nq\\nd\\no\\no\\nd\\no\\nd\\nd\\nd\\nd\\nd\\nd\\nCM\\nq\\ncd\\no\\nd\\nd\\no\\nq\\nT-\\nco\\ni\\nCM\\nfx\\nLO\\nCD\\nCT)\\nT_\\nT\u00e2\u0080\u0094\\n0\\n0\\no\\no\\nq\\n.2 75\\nU)\\n0\\nx.\\no o c\\nQ. c\\nC -Q\\nk\\no\\n3\\n0\\nill\\n\u00e2\u0080\u0098c\\nx.\\n0\\nro\\n\u00e2\u0096\u00a0k*\\no\\nC\\nq o cc\\nq\\nq\\n8.0 National Greenhouse Gas Emissions 8-7", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0181.jp2"}, "182": {"fulltext": "Figure 8-1. U.S. Carbon Dioxide Emissions by Sector (1994)\\nNational Air Pollutant Emission Trends, 1990-1998\\nCtJ\\nmm\\n3\\n\u00e2\u0080\u00a2a\\nc\\nc\\no\\n(0\\nc\\nD\\n\u00e2\u0096\u00a0a\\no\\nL.\\na)\\n.2\\n*SZ\\nCO\\nt\\no\\na\\n35\\na)\\nE\\no\\n3\\nT5\\nc\\nro\\nor\\no\\nC\\nD\\n8-8 5.0 National Criteria Pollutant Estimation Methodologies\\nTransportation\\n30%", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0182.jp2"}, "183": {"fulltext": "Figure 8-2. Carbon Dioxide Emissions from Industry (1994)\\nNational Air Pollutant Emission Trends, 1990-1998\\nif)\\n1)\\ni\u00e2\u0080\u0094\\nD\\n-4\u00e2\u0080\u0094\u00c2\u00bb\\nX\\n5.0 National Criteria Pollutant Estimation Methodologies 8-9", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0183.jp2"}, "184": {"fulltext": "Figure 8-3. U.S. Carbon Dioxide Emissions by\\nEnd-Use Sector in 1994\\nNational Air Pollutant Emission Trends, 1990-1998\\n8-10 5.0 National Criteria Pollutant Estimation Methodologies", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0184.jp2"}, "185": {"fulltext": "Chapter 9.0 International Emissions\\n9.1 WHAT DATA ARE PRESENTED IN\\nTHIS CHAPTER?\\nThis chapter presents the 1996 European emission\\nestimates for the pollutants carbon monoxide (CO), nitrogen\\noxides (NO x sulfur dioxide (SO,), nonmethane volatile\\norganic compounds (NMVOCs), methane (CH 4 carbon\\ndioxide (C0 2 nitrous oxide (N,0), and ammonia (NH 3 and\\nthe 1995 Canadian emission estimates for the pollutants CO,\\nNO x volatile organic compounds (VOC), S0 2 total particulate\\n(TP), particulate matter (PM) less than 10 microns in diameter\\n(PM 10 and PM less than 2.5 microns in diameter (PM 2 5\\n9.2 WHAT EUROPEAN EMISSIONS ARE\\nPRESENTED?\\nIn 1993, the European Union launched the European\\nEnvironment Agency (EEA) with a mandate to orchestrate,\\ncross-check, and put to strategic use information relevant to\\nprotecting and improving Europe\u00e2\u0080\u0099s environment. 1 CORINAIR\\n(Coordination of Environmental Air) is the air emission\\ninventory for Europe The CORINAIR project is part of the\\nwork program of the EEA. The EEA designated the European\\nTopic Center on Air Emissions (ETC/AEM) to perform the\\nCORINAIR project by assisting participating countries to\\nreport their national inventories as required under international\\nobligations. Based on these reports the ETC/AEM prepares\\nthe European air emission inventory and database. 2\\nThe countries that submitted 1996 data on emissions of\\nozone precursors and acidifying pollutants to CORINAIR\\ninclude Austria, the Czech Republic, Denmark, Finland,\\nFrance, Germany, Greece, Ireland, Luxembourg, the\\nNetherlands, Norway, Slovenia, and the United Kingdom. In\\naddition, the following countries submitted 1996 data on\\nemissions of greenhouse gases to the United Nations\\nFramework Convention on Climate Change (UNFCCC):\\nAustria, Belgium, the Czech Republic, Denmark, Estonia,\\nFinland, France, Germany, Greece, Ireland, Luxembourg, the\\nNetherlands, Norway, Slovenia, Spain, Sweden, and the\\nUnited Kingdom.\\nTable 9-1 shows European national total emissions for\\n1996 for the following pollutants: S0 2 NO x NMVOC, CH 4\\nCO, CO, and NH 3 Tables 9-2 through 9-8 present 1996\\ncountry-level summary data by CORINAIR/EMEP\\n(Cooperative Programme for Monitoring and Evaluation of the\\nLong Range Transmission of Air Pollutants in Europe) source\\ncategory for S0 2 NO x NMVOC, CO, and NH 3 The\\nCORINAIR/EMEP source categories include:\\nCombustion in energy and transformation industries\\nNonindustrial combustion plants\\nCombustion in manufacturing industry\\nProduction processes\\nExtraction and distribution of fossil fuels/geothermal\\nenergy\\nSolvent and other product use\\nRoad transport\\nOther mobile sources and machinery\\nWaste treatment and disposal\\nAgriculture and forestry, land use and woodstock\\nchange\\nNature\\nBecause some countries included estimates of NMVOC and\\nCO, emissions in the Nature and the Agriculture categories,\\nthese tables include a \u00e2\u0080\u009cComparable Total\u00e2\u0080\u009d line, omitting these\\ntwo categories for each country.\\nTables 9-9 to 9-13 present 1996 country-level summary\\ndata by EEA source category for CH 4 CO,, and N 2 0. The\\nEEA source categories include Energy, Industry, Transport,\\nAgriculture, Waste, and Other.\\n9.3 WHAT CANADIAN EMISSIONS ARE\\nPRESENTED?\\nThe criteria air pollutant annual emissions data for Canada\\nwere provided by Environment Canada 3 for 1995. Emissions\\nwere provided for CO, NO x VOC, SO,, TP, PM 10 and PM, 5\\nTable 9-14 presents the emission estimates for Canada by\\nmajor source category. Table 9-15 presents the emissions for\\nCanada by Province.\\n9.0 International Emissions 9-1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0185.jp2"}, "186": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\n9.4 REFERENCES\\n1. European Environment Agency, at http://org.eea.eu.int/. January 2000.\\n2. \u00e2\u0080\u009cETC/Air Emissions\u00e2\u0080\u009d (Database version 2.2, 10/25/99), at http://warehouse.eea.eu.int/, European Topic Centre on Air\\nEmissions, European Environment Agency, Copenhagen, Denmark. October 1999.\\n3. Environment Canada, at http://www.ec.gc.ca, August 1999.\\n4. \u00e2\u0080\u009cPopulation for the Countries of the World: 1996,\u00e2\u0080\u009d at gopher://gopher.undp.org. United Nations Population Division.\\nAugust 1999.\\n5. \u00e2\u0080\u009cWorld Emissions Tables,\u00e2\u0080\u009d at http://projects.dnmi.no/%7emep/emis_tables/. Meteorological Synthesizing Centre-\\nWest, EMEP. July 1999.\\n9-2 9.0 International Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0186.jp2"}, "187": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-1. 1996 Emission Estimates for Europe by Country and Pollutant\\n(thousand short tons; except C0 2 [million short tons])\\nCountry\\nPopulation\\n(million)\\nO\\nro\\nNO x\\nNMVOC\\nch 4\\nCO\\nCNJ\\nO\\no\\nnh 3\\nArmenia\\n3.6\\n2\\n12\\n20\\nNA\\n138\\nNA\\n0\\nAustria\\n8.1\\n57\\n180\\n288\\n493\\n1,125\\nNA\\n84\\nBelarus\\n10.3\\n271\\n191\\n362\\nNA\\n1,339\\nNA\\n4\\nBelgium\\n10.1\\n265\\n368\\n357\\nNA\\n1,369\\nNA\\n107\\nBulgaria\\n8.4\\n1,565\\n285\\n162\\n546\\n676\\nNA\\n91\\nCroatia\\n4.5\\n64\\n74\\n87\\n148\\n413\\n20\\n25\\nCyprus\\n0.8\\n51\\n23\\nNA\\nNA\\nNA\\n7\\nNA\\nCzech Republic\\n10.2\\n1,043\\n476\\n313\\n632\\n977\\n142\\n89\\nDenmark\\n5.2\\n205\\n317\\n150\\n468\\n658\\n80\\n109\\nFinland\\n5.1\\n116\\n294\\n191\\n281\\n474\\n73\\n39\\nFrance\\n58.3\\n1,136\\n1,809\\n2,833\\n3,142\\n9,755\\n366\\n736\\nGermany\\n81.9\\n1,701\\n2,080\\n2,069\\n3,939\\n7,404\\n1,013\\n715\\nGreece\\n10.4\\n599\\n412\\n451\\n504\\n1,470\\n101\\nNA\\nHungary\\n10.0\\n742\\n216\\n165\\nNA\\n801\\n74\\n86\\nIreland\\n3.6\\n162\\n133\\n114\\n811\\n338\\n40\\n141\\nLatvia\\n2.5\\n65\\n39\\n45\\n103\\n194\\n12\\nNA\\nLithuania\\n3.7\\n103\\n72\\n96\\n314\\n344\\n21\\n40\\nLuxembourg\\n0.4\\n9\\n24\\n20\\n25\\n114\\n8\\n8\\nNetherlands\\n15.6\\n149\\n552\\n399\\n1,359\\n995\\n209\\n161\\nNorway\\n4.3\\n37\\n246\\n407\\n535\\n794\\n45\\n29\\nPoland\\n38.6\\n2,610\\n1,272\\n844\\n2,016\\n5,332\\nNA\\n408\\nRussian Federation\\n148.1\\n2,960\\n2,719\\n2,840\\n3,457\\n10,265\\n1,653\\n826\\nSlovakia\\n5.3\\n250\\n143\\n116\\n330\\n381\\n50\\n55\\nSlovenia\\n1.9\\n121\\n77\\nNA\\nNA\\n105\\n17\\nNA\\nSweden\\n8.8\\n91\\n333\\n492\\n327\\n1,193\\n69\\n67\\nSwitzerland\\n7.2\\n33\\n143\\n224\\n259\\n535\\nNA\\n78\\nUkraine\\n51.6\\n1,425\\n515\\n791\\nNA\\n2,830\\nNA\\nNA\\nUnited Kingdom\\n58.1\\n2,223\\n2,237\\n2,255\\n4,094\\n5,511\\n654\\n352\\nYugoslavia\\n10.3\\n478\\n63\\nNA\\nNA\\nNA\\nNA\\nNA\\nTotal\\n586.9\\n18,533\\n15,305\\n16,091\\n23,783\\n55,530\\n4,654\\n4,250\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource of population data: United Nations Population Division 4\\nSource of emission data: EMEP, Meteorological Synthesizing Centre-West 5\\n9.0 International Emissions 9-3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0187.jp2"}, "188": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-2. 1996 Emission Estimates for Austria and the Czech Republic by\\nCORINAIR/EMEP Source Category and Pollutant\\n(thousand short tons)\\nAustria\\nCM\\no\\nf\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n9\\n11\\n0\\n1\\n0\\nNonindustrial combustion plants\\n18\\n22\\n46\\n478\\n1\\nCombustion in manufacturing industry\\n10\\n17\\n1\\n6\\n0\\nProduction processes\\n15\\n21\\n25\\n291\\n0\\nExtraction and distribution of fossil fuels/geothermal energy\\n1\\n0\\n4\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n147\\n0\\n0\\nRoad transport\\n3\\n93\\n58\\n335\\n3\\nOther mobile sources and machinery\\n0\\n8\\n3\\n8\\n0\\nWaste treatment and disposal\\n0\\n0\\n1\\n5\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n7\\n3\\n2\\n80\\nNature\\n0\\n1\\n181\\n0\\n1\\nTotal\\n57\\n180\\n469\\n1,126\\n85\\nComparable Total\\n57\\n178\\n285\\n1,126\\n84\\nCzech Republic\\ntf)\\nO\\nro\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n715\\n131\\n5\\n17\\n0\\nNonindustrial combustion plants\\n186\\n49\\n48\\n366\\n0\\nCombustion in manufacturing industry\\n130\\n45\\n10\\n271\\n0\\nProduction processes\\n2\\n1\\n31\\n1\\n2\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n3\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n131\\n0\\n0\\nRoad transport\\n6\\n191\\n72\\n263\\n1\\nOther mobile sources and machinery\\n3\\n59\\n13\\n59\\n0\\nWaste treatment and disposal\\n0\\n1\\n0\\n0\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n0\\n0\\n87\\nNature\\n0\\n0\\n45\\n0\\n1\\nTotal\\n1,043\\n476\\n358\\n977\\n90\\nComparable Total\\n1,043\\n476\\n313\\n977\\n89\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nNegative emissions represent a sink for greenhouse gas.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9-4 9.0 International Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0188.jp2"}, "189": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-3. 1996 Emission Estimates for Denmark and Finland by\\nCORINAIR/EMEP Source Category and Pollutant\\n(thousand short tons)\\nDenmark\\nS0 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n160\\n142\\n2\\n12\\n0\\nNonindustrial combustion plants\\n13\\n8\\n13\\n133\\n0\\nCombustion in manufacturing industry\\n13\\n16\\n1\\n7\\n0\\nProduction processes\\n3\\n1\\n12\\n0\\n0\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n8\\n48\\n0\\nSolvent and other product use\\n0\\n0\\n23\\n0\\n0\\nRoad transport\\n2\\n87\\n67\\n391\\n1\\nOther mobile sources and machinery\\n8\\n62\\n13\\n66\\n0\\nWaste treatment and disposal\\n0\\n2\\n1\\n1\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n1\\n0\\n108\\nNature\\n0\\n0\\n10\\n0\\n0\\nTotal\\n198\\n318\\n150\\n659\\n109\\nComparable Total\\n198\\n318\\n139\\n659\\n109\\nFinland\\nso 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n48\\n48\\n0\\n8\\n0\\nNonindustrial combustion plants\\n15\\n15\\n35\\n73\\n0\\nCombustion in manufacturing industry\\n27\\n36\\n0\\n47\\n0\\nProduction processes\\n23\\n8\\n12\\n11\\n1\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n10\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n35\\n0\\n0\\nRoad transport\\n1\\n189\\n75\\n331\\n0\\nOther mobile sources and machinery\\n2\\n0\\n20\\n3\\n0\\nWaste treatment and disposal\\n0\\n0\\n2\\n0\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n0\\n0\\n37\\nNature\\n0\\n0\\n0\\n0\\n0\\nTotal\\n116\\n297\\n190\\n473\\n39\\nComparable Total\\n116\\n297\\n190\\n473\\n39\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99 y\\n9.0 International Emissions 9-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0189.jp2"}, "190": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-4. 1996 Emission Estimates for France and Germany by\\nCORINAIR/EMEP Source Category and Pollutant\\n(thousand short tons)\\nFrance\\nS0 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n394\\n140\\n4\\n18\\n0\\nNonindustrial combustion plants\\n95\\n118\\n237\\n2,044\\n0\\nCombustion in manufacturing industry\\n295\\n170\\n12\\n615\\n0\\nProduction processes\\n80\\n19\\n95\\n638\\n31\\nExtraction and distribution of fossil fuels/geothermal energy\\n15\\n0\\n110\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n634\\n0\\n0\\nRoad transport\\n129\\n988\\n985\\n4,980\\n8\\nOther mobile sources and machinery\\n18\\n410\\n158\\n466\\n0\\nWaste treatment and disposal\\n18\\n25\\n31\\n256\\n4\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n20\\n0\\n848\\nNature\\n0\\n3\\n413\\n84\\n0\\nTotal\\n1,044\\n1,873\\n2,700\\n9,100\\n891\\nComparable Total\\n1,044\\n1,870\\n2,266\\n9,017\\n891\\nGermany\\nso 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n931\\n377\\n8\\n129\\n3\\nNonindustrial combustion plants\\n323\\n179\\n97\\n1,737\\n0\\nCombustion in manufacturing industry\\n315\\n247\\n9\\n742\\n1\\nProduction processes\\n68\\n14\\n139\\n649\\n9\\nExtraction and distribution of fossil fuels/geothermal energy\\n17\\n0\\n46\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n1,113\\n0\\n1\\nRoad transport\\n34\\n999\\n600\\n3,954\\n35\\nOther mobile sources and machinery\\n13\\n265\\n57\\n193\\n0\\nWaste treatment and disposal\\n0\\n0\\n0\\n0\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n0\\n0\\n666\\nNature\\n0\\n0\\n425\\n0\\n0\\nTotal\\n1,702\\n2,080\\n2,495\\n7,404\\n715\\nComparable Total\\n1,702\\n2,080\\n2,069\\n7,404\\n715\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9-6 9.0 International Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0190.jp2"}, "191": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-5. 1996 Emission Estimates for Greece and Ireland by\\nCORINAIR/EMEP Source Category and Pollutant\\n(thousand short tons)\\nGreece\\nS0 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n435\\n91\\n4\\n8\\n0\\nNonindustrial combustion plants\\n16\\n9\\n11\\n156\\n0\\nCombustion in manufacturing industry\\n88\\n26\\n8\\n17\\n0\\nProduction processes\\n18\\n37\\n20\\n23\\n1\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n18\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n64\\n0\\n0\\nRoad transport\\n10\\n114\\n208\\n1,038\\n1\\nOther mobile sources and machinery\\n28\\n110\\n19\\n144\\n0\\nWaste treatment and disposal\\n0\\n2\\n9\\n13\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n5\\n53\\n127\\n85\\nNature\\n0\\n0\\n0\\n0\\n0\\nTotal\\n596\\n394\\n414\\n1,527\\n87\\nComparable Total\\n596\\n394\\n362\\n1,527\\n87\\nIreland\\nCN\\no\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n102\\n46\\n0\\n4\\n0\\nNonindustrial combustion plants\\n31\\n9\\n6\\n62\\n0\\nCombustion in manufacturing industry\\n36\\n11\\n0\\n2\\n0\\nProduction processes\\n0\\n0\\n1\\n0\\n0\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n4\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n24\\n0\\n0\\nRoad transport\\n6\\n51\\n65\\n262\\n0\\nOther mobile sources and machinery\\n2\\n10\\n2\\n6\\n0\\nWaste treatment and disposal\\n0\\n0\\n0\\n1\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n93\\n0\\n136\\nNature\\n0\\n0\\n0\\n0\\n0\\nTotal\\n178\\n127\\n196\\n337\\n137\\nComparable Total\\n178\\n127\\n103\\n337\\n137\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9.0 International Emissions 9-7", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0191.jp2"}, "192": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-6. 1996 Emission Estimates for Luxembourg and the Netherlands\\nby CORINAIR/EMEP Source Category and Pollutant\\n(thousand short tons)\\nLuxembourg\\nS0 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n0\\n0\\n0\\n0\\n0\\nNonindustrial combustion plants\\n1\\n1\\n1\\n9\\n0\\nCombustion in manufacturing industry\\n7\\n8\\n0\\n44\\n0\\nProduction processes\\n0\\n0\\n1\\n9\\n2\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n2\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n4\\n0\\n0\\nRoad transport\\n1\\n11\\n9\\n45\\n0\\nOther mobile sources and machinery\\n0\\n1\\n1\\n3\\n0\\nWaste treatment and disposal\\n0\\n0\\n0\\n0\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n1\\n0\\n6\\nNature\\n0\\n0\\n1\\n0\\n0\\nTotal\\n9\\n22\\n20\\n111\\n8\\nComparable Total\\n9\\n22\\n18\\n111\\n8\\nNetherlands\\nCM\\no\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n53\\n71\\n2\\n20\\n0\\nNonindustrial combustion plants\\n3\\n52\\n13\\n115\\n0\\nCombustion in manufacturing industry\\n34\\n61\\n8\\n72\\n0\\nProduction processes\\n26\\n18\\n78\\n184\\n4\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n31\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n94\\n0\\n1\\nRoad transport\\n12\\n233\\n148\\n536\\n0\\nOther mobile sources and machinery\\n19\\n100\\n13\\n41\\n0\\nWaste treatment and disposal\\n1\\n2\\n7\\n9\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n17\\n3\\n19\\n155\\nNature\\n0\\n1\\n0\\n9\\n7\\nTotal\\n149\\n554\\n399\\n1,005\\n167\\nComparable Total\\n149\\n553\\n395\\n996\\n161\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9-8 9.0 International Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0192.jp2"}, "193": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-7. 1996 Emission Estimates for Norway and Slovenia by\\nCORINAIR/EMEP Source Category and Pollutant\\n(thousand short tons)\\nNorway\\nS0 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n1\\n32\\n2\\n7\\n0\\nNonindustrial combustion plants\\n2\\n3\\n11\\n153\\n0\\nCombustion in manufacturing industry\\n6\\n9\\n1\\n8\\n0\\nProduction processes\\n23\\n10\\n20\\n44\\n0\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n232\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n52\\n0\\n0\\nRoad transport\\n2\\n72\\n68\\n488\\n1\\nOther mobile sources and machinery\\n3\\n109\\n19\\n65\\n0\\nWaste treatment and disposal\\n0\\n7\\n1\\n1\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n0\\n0\\n28\\nNature\\n0\\n0\\n0\\n0\\n0\\nTotal\\n37\\n243\\n406\\n766\\n29\\nComparable Total\\n37\\n243\\n406\\n766\\n29\\nSlovenia\\nso 2\\nNO x\\nNMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n105\\n18\\n0\\n1\\n0\\nNonindustrial combustion plants\\n8\\n3\\n0\\n4\\n0\\nCombustion in manufacturing industry\\n6\\n3\\n0\\n0\\n0\\nProduction processes\\n0\\n0\\n0\\n0\\n0\\nExtraction and distribution of fossil fuels/geothermal energy\\n0\\n0\\n0\\n0\\n0\\nSolvent and other product use\\n0\\n0\\n0\\n0\\n0\\nRoad transport\\n1\\n51\\n0\\n97\\n0\\nOther mobile sources and machinery\\n0\\n3\\n0\\n2\\n0\\nWaste treatment and disposal\\n0\\n0\\n0\\n0\\n0\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n0\\n0\\n0\\nNature\\n0\\n0\\n0\\n0\\n0\\nTotal\\n121\\n77\\n0\\n105\\n0\\nComparable Total\\n121\\n77\\nNA\\n105\\nNA\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 4\\n9.0 International Emissions 9-9", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0193.jp2"}, "194": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-8. 1996 Emission Estimates for the United Kingdom by\\nCORINAIR/EMEP Source Category and Pollutant\\n(thousand short tons)\\nUnited Kingdom\\nCM\\no\\nCO\\nNO x NMVOC\\nCO\\nnh 3\\nCombustion in energy and transformation industries\\n1,598\\n613\\n9\\n228\\n5\\nNonindustrial combustion plants\\n141\\n126\\n37\\n258\\n0\\nCombustion in manufacturing industry\\n287\\n186\\n8\\n37\\n0\\nProduction processes\\n109\\n5\\n201\\n50\\n0\\nExtraction and distribution of fossil fuels/geothermal energy\\n8\\n1\\n323\\n4\\n0\\nSolvent and other product use\\n0\\n0\\n666\\n0\\n0\\nRoad transport\\n41\\n1,065\\n699\\n3,637\\n11\\nOther mobile sources and machinery\\n50\\n267\\n132\\n879\\n0\\nWaste treatment and disposal\\n1\\n8\\n51\\n27\\n12\\nAgriculture and forestry, land use and woodstock change\\n0\\n0\\n88\\n0\\n329\\nNature\\n0\\n0\\n0\\n0\\n0\\nTotal\\n2,235\\n2,271\\n2,215\\n5,121\\n357\\nComparable Total\\n2,235\\n2,271\\n2,127\\n5,121\\n357\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9-10 9.0 International Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0194.jp2"}, "195": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-9. 1996 Emission Estimates for Austria, Belgium, Czech Republic,\\nand Denmark by EEA Source Category and Pollutant\\n(thousand short tons; except C0 2 [million short tons])\\nAustria\\nch 4\\no\\no\\nro\\nN 2 0\\nEnergy\\n0\\n13\\n0\\nIndustry\\n0\\n21\\n1\\nTransport\\n2\\n17\\n2\\nAgriculture\\n227\\n0\\n4\\nWaste\\n241\\n0\\n0\\nOther\\n22\\n4\\n2\\nTotal\\n492\\n54\\n8\\nBelgium\\nch 4\\nCM\\nO\\no\\nN 2 0\\nEnergy\\n0\\n34\\n2\\nIndustry\\n3\\n45\\n18\\nTransport\\n4\\n25\\n1\\nAgriculture\\n389\\n0\\n12\\nWaste\\n212\\n0\\n0\\nOther\\n51\\n37\\n7\\nTotal\\n658\\n141\\n41\\nCzech Republic\\nch 4\\nC0 2\\nN 2 0\\nEnergy\\nNA\\nNA\\nNA\\nIndustry\\nNA\\nNA\\nNA\\nTransport\\nNA\\nNA\\nNA\\nAgriculture\\nNA\\nNA\\nNA\\nWaste\\nNA\\nNA\\nNA\\nOther\\nNA\\nNA\\nNA\\nTotal\\nNA\\nNA\\nNA\\nDenmark\\nCH,\\nCO,\\nN,0\\nEnergy\\n2\\n49\\n2\\nIndustry\\n1\\n8\\n0\\nTransport\\n3\\n13\\n1\\nAgriculture\\n354\\n0\\n33\\nWaste\\n81\\n0\\n0\\nOther\\n28\\n10\\n1\\nTotal\\n469\\n80\\n37\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nNegative emissions represent a sink for greenhouse gas.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9.0 International Emissions 9-11", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0195.jp2"}, "196": {"fulltext": "National Air Pollutant Emission Trends 1900 1998\\nTable 9-10. 1996 Emission Estimates for Estonia, Finland, France, and\\nGermany by EEA Source Category and Pollutant\\n(thousand short tons; except C0 2 [million short tons])\\nEstonia\\nch 4\\nCM\\nO\\no\\nn 2 o\\nEnergy\\n0\\n22\\n0\\nIndustry\\n0\\n0\\n0\\nTransport\\n0\\n2\\n0\\nAgriculture\\n33\\n0\\n0\\nWaste\\n34\\n0\\n0\\nOther\\n2\\n-3\\n1\\nTotal\\n70\\n20\\n1\\nFinland\\nch 4\\nCM\\nO\\no\\nn 2 o\\nEnergy\\n2\\n30\\n3\\nIndustry\\n7\\n16\\n5\\nTransport\\n3\\n12\\n2\\nAgriculture\\n90\\n0\\n10\\nWaste\\n176\\n0\\n0\\nOther\\n18\\n15\\n1\\nTotal\\n298\\n73\\n20\\nFrance\\nch 4\\nCM\\no\\no\\nN 2 0\\nEnergy\\n2\\n66\\n2\\nIndustry\\n9\\n109\\n91\\nTransport\\n21\\n149\\n9\\nAgriculture\\n1,725\\n0\\n193\\nWaste\\n675\\n4\\n4\\nOther\\n565\\n48\\n27\\nTotal\\n2,997\\n376\\n326\\nGermany\\nch 4\\nC0 2\\nN 2 0\\nEnergy\\n8\\n398\\n14\\nIndustry\\n9\\n182\\n99\\nTransport\\n32\\n192\\n23\\nAgriculture\\n1,712\\n2\\n94\\nWaste\\n873\\n0\\n4\\nOther\\n1,305\\n204\\n12\\nTotal\\n3,939\\n976\\n247\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nNegative emissions represent a sink for greenhouse gas.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9-12 9.0 International Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0196.jp2"}, "197": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-11. 1996 Emission Estimates for Greece, Ireland, Luxembourg, and\\nNetherlands by EEA Source Category and Pollutant\\n(thousand short tons; except C0 2 [million short tons])\\nGreece\\nch 4\\nC0 2\\nn 2 o\\nEnergy\\n0\\n50\\n3\\nIndustry\\n3\\n21\\n3\\nTransport\\n7\\n19\\n1\\nAgriculture\\n309\\n0\\n22\\nWaste\\n125\\n0\\n0\\nOther\\n64\\n11\\n2\\nTotal\\n505\\n101\\n33\\nIreland\\nch 4\\nco 2\\nN 2 0\\nEnergy\\n0\\n15\\n2\\nIndustry\\n0\\n6\\n3\\nTransport\\n2\\n7\\n1\\nAgriculture\\n722\\n0\\n21\\nWaste\\n112\\n0\\n0\\nOther\\n45\\n3\\n2\\nTotal\\n881\\n31\\n29\\nLuxembourg\\nch 4\\nC0 2\\nN 2 0\\nEnergy\\n0\\n1\\n0\\nIndustry\\n0\\n4\\n0\\nTransport\\n0\\n1\\n0\\nAgriculture\\n19\\n0\\n1\\nWaste\\n4\\n0\\n0\\nOther\\n3\\n1\\n0\\nTotal\\n26\\n7\\n1\\nNetherlands\\nch 4\\nC0 2\\nn 2 o\\nEnergy\\n6\\n63\\n0\\nIndustry\\n8\\n50\\n35\\nTransport\\n7\\n37\\n8\\nAgriculture\\n512\\n0\\n30\\nWaste\\n526\\n2\\n1\\nOther\\n242\\n51\\n5\\nTotal\\n1302\\n204\\n79\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nNegative emissions represent a sink for greenhouse gas.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9.0 International Emissions 9-13", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0197.jp2"}, "198": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nTable 9-12. 1996 Emission Estimates for Norway, the Slovenia, Spain, and\\nSweden by EEA Source Category and Pollutant\\n(thousand short tons; except C0 2 [million short tons])\\nNorway\\nch 4\\nCM\\no\\no\\nN 2 0\\nEnergy\\n3\\n11\\n0\\nIndustry\\n1\\n13\\n6\\nTransport\\n3\\n16\\n1\\nAgriculture\\n119\\n0\\n10\\nWaste\\n214\\n0\\n0\\nOther\\n39\\n-14\\n0\\nTotal\\n380\\n26\\n18\\nSlovenia\\nch 4\\nco 2\\nn 2 o\\nEnergy\\nNA\\nNA\\nNA\\nIndustry\\nNA\\nNA\\nNA\\nTransport\\nNA\\nNA\\nNA\\nAgriculture\\nNA\\nNA\\nNA\\nWaste\\nNA\\nNA\\nNA\\nOther\\nNA\\nNA\\nNA\\nTotal\\nNA\\nNA\\nNA\\nSpain\\nch 4\\nO\\nO\\nro\\nn 2 o\\nEnergy\\n13\\n78\\n11\\nIndustry\\n7\\n70\\n15\\nTransport\\n12\\n72\\n4\\nAgriculture\\n1,128\\n0\\n66\\nWaste\\n903\\n0\\n0\\nOther\\n783\\n0\\n3\\nTotal\\n2,846\\n220\\n99\\nSweden _CH 4 _COj_ N 2 Q\\nEnergy\\n2\\n16\\n2\\nIndustry\\n6\\n20\\n7\\nTransport\\n21\\n22\\n2\\nAgriculture\\n180\\n0\\n18\\nWaste\\n67\\n0\\n0\\nOther\\n12\\n-22\\n1\\nTotal\\n288\\n35\\n29\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nNegative emissions represent a sink for greenhouse gas.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\n9-14 9.0 International Emissions", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0198.jp2"}, "199": {"fulltext": "National Air Pollutant Emission Trends, 1900 -1998\\nTable 9-13. 1996 Emission Estimates for the United Kingdom by EEA\\nSource Category and Pollutant\\n(thousand short tons; except C0 2 [million short tons])\\nUnited Kingdom\\nch 4\\nco\\nN 0\\nEnergy\\n19\\n220\\n7\\nIndustry\\n14\\n116\\n78\\nTransport\\n25\\n135\\n11\\nAgriculture\\n1,120\\n0\\n106\\nWaste\\n999\\n0\\n1\\nOther\\n924\\n170\\n2\\nTotal\\n3,101\\n642\\n206\\nNote(s): NA not available. Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nNegative emissions represent a sink for greenhouse gas.\\nSource: ETC/Air Emissions (Database version 2.2, 10/25/99) 2\\nTable 9-14.\\n1995 Emissions for Canada by Major Source Category\\n(thousand short tons)\\nSource Category\\nco\\nNO x\\nvoc\\nSO, TP\\nPM 10\\nPM ?,s\\nIndustrial Sources\\n2,400\\n684\\n1,037\\n2,149 685\\n317\\n189\\nNonindustrial Fuel Combustion\\n1,189\\n367\\n449\\n624 248\\n197\\n173\\nTransportation\\n7,394\\n1,422\\n810\\n150 108\\n105\\n92\\nIncineration\\n51\\n3\\n7\\n1 3\\n2\\n1\\nMiscellaneous\\n16\\n1\\n606\\n0 24\\n16\\n10\\nOpen Sources\\n7,380\\n239\\n1,033\\n1 16,222\\n5,920\\n1,209\\nTotal\\n18,880\\n2,716\\n3,941\\n2,925 17,289\\n5,920\\n1,675\\nNote(s): Totals presented in this table may not equal the sum of the individual source categories due to rounding.\\nSource: Environment Canada 3\\nTable 9-15. 1995 Emissions for Canada by Province\\n(thousand short tons)\\nSource Category\\nCO\\nNOx\\nVOC\\nS02\\nTP\\nPMio\\n_\\nAlberta\\n2,206\\n720\\n841\\n670\\n5,573\\n1,742\\n296\\nBritish Columbia\\n1,904\\n291\\n290\\n194\\n713\\n334\\n193\\nManitoba\\n1,718\\n120\\n262\\n403\\n1,085\\n449\\n147\\nNew Brunswick\\n357\\n69\\n72\\n127\\n501\\n137\\n39\\nNewfoundland\\n262\\n47\\n58\\n72\\n368\\n113\\n34\\nNorthwest Territories\\n2680\\n95\\n382\\n17\\n359\\n283\\n228\\nNova Scotia\\n349\\n81\\n87\\n184\\n459\\n127\\n38\\nOntario\\n4,186\\n613\\n906\\n697\\n3,867\\n1,151\\n287\\nPrince Edward Island\\n59\\n9\\n11\\n3\\n100\\n27\\n5\\nQuebec\\n2,728\\n422\\n537\\n412\\n2,375\\n713\\n195\\nSaskatchewan\\n2,173\\n236\\n459\\n145\\n1,812\\n209\\n190\\nYukon\\n259\\n13\\n36\\n0\\n77\\n36\\n22\\nTotal\\n18,880\\n2,716\\n3,941\\n2,925\\n17,289\\n5,920\\n1,675\\nSource: Environment Canada 3\\n9.0 International Emissions 9-15", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0199.jp2"}, "200": {"fulltext": "[This page intentionally left blank.]", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0200.jp2"}, "201": {"fulltext": "Appendix A\\nNational Emissions (1970 to\\n1998) by Tier 3 Source Category\\nand Pollutant\\nAppendix A National Emissions (1970 to 1998) A-l", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0201.jp2"}, "202": {"fulltext": "Table A-1. Carbon Monoxide Emissions\\n(thousand short tons)\\nNational Air Pollutant Emission Trends, 1900-1998\\nooK- tr^or^ tcooLncDC\\no LO\\nCT 3 CM\\ns^Mc\\\\in(D ototD^ni/)t iwo) 0 )NN(OffN 0 wOQOcynQt )in\\n0) 5wi-coio Nou)nn\u00c2\u00aeoiT-T-winoooO)0)u) ffl o cm dm\\nCD CM -r- O CO CM O M; 0)_ C\\\\| CM -r-\\nt-T c^r nrr c\\\\T\\n^-pr-iocoio --oior--i s -DpincoYtr s i s t x^ro:co\u00e2\u0080\u0099-~oOM r -LOLoo ioini s -ooincppDp\\nm^ MT-inn3ocDncoifiOi-i-inMoQ (oKn c\\\\jco r t- oo p o co\\nCD CD CM CD CO CM CM t-CO 0^-^CM -t- y- y- 00 I s\\nCO* Co\\nCO LO\\nO CO CO CO CO\\nCO CO CM\\ncocoinr-cocMCoco 3-r~.CDcoooococoCMCoincMoococo D-cp\\n^T-t-mmiooNNM(N(D cd cm cm t- o) co cm\\nCO rt CJ) C\\\\| C\\\\J CM i\u00e2\u0080\u0094 COCO\\nco co cm y-t\\nCM O O CO ,1 s o- Cp\\nt- co jo c\\\\j\\nCO CO\\nY- CO\\n0 Tf\\nCO CM\\nffl tJKOOWffiT-OCMOOO^\\nMo ootDn^opT-T-inw\\nt- CO CO CO CO\\nco cm\\nO co t- o O\\no CD O O CO o\\nCM CO CO CO CM\\nCD\\nOOO\u00e2\u0080\u0099 CM0)C0inCM\\n0 CM y- T-\\no o\\no r~\\nr- mi-\\nCO 00\\nCO\\ncm\\n\u00e2\u0080\u00a2Yf CO\\nCMOOintO\u00c2\u00ab fflr-inNin(OUHDMinO)0) T TCOCONOM COMCl l OM)NOOO) l OJOC)\\nKini-LOLnl\u00c2\u00a3?CDC ^-CD M-C)^^iO ^CDCD r^CMCM CM CO y- y- y- CO JC CO CM\\nCO CM O CO CM CM \u00e2\u0080\u0098O i-(DO t CMCMi- y^ ,_ y- CDCO\\ny- co co y-T\\ncp\\nCO\\nCO\\nCT)\\n7-\\nco\\n7\u00e2\u0080\u0094\\nco\\nCM\\nCo\\nYt\\nT\u00e2\u0080\u0094\\nxf\\nLO\\no\\nCO\\nCM\\nco\\nCM\\no\\nCO\\nY-C\\nO\\nCO\\nLO\\nI s\\n1\u00c2\u00b0\\nCM\\nX}-\\no\\nLO\\nCO\\n1\u00e2\u0080\u0094\\nLO\\nYt\\nin\\no\\nco\\no\\nCO\\nCM\\no\\nCO\\nO)\\nXj-\\nCD\\nLO\\no\\no\\nYt\\nCO\\n7\u00e2\u0080\u0094\\nLO\\n\u00e2\u0096\u00a0M-\\nCM\\no\\nCO\\nco\\nco\\nCM\\nO)\\nCM\\nxr\\no\\n7-\\nD~\\nLO\\nxf\\nCO\\nCO\\nco\\nCM\\nLO\\nLO\\nK\\no\\nr-\\nCM\\nCO\\nCM\\n\u00c2\u00abo\\nCM\\nY\u00e2\u0080\u0094\\nCO\\nCO\\nCM\\nI s\\nCD\\nCM\\nCO\\nCM\\nLO\\n7\u00e2\u0080\u0094\\nN.\\nco\\nxr\\nr-\\nCO\\nCM\\nCO\\nCM\\no-\\nO\\nin\\nCO\\nO)\\nr-\\nCO\\nm\\nY-.\\nCO\\nCM\\nYj-\\n7-\\nCO\\nCO\\nYt\\nCO\\nCO\\nCM\\nCO\\nCM\\nY*\u00c2\u00bb\\nI\\nco\\nco\\no\\np\\nco\\nI s\\nI s\\np)\\nO\\n1\u00e2\u0080\u0094\\nin\\n7-\\nK\\nco\\nxj-\\nLO\\nCM\\nCM\\nCO\\nCM\\nCM\\nX\\nCO\\nLO\\np\\nco\\nLO\\nco\\nSi\\nco\\noo\\nY\u00e2\u0080\u009c\\nxf\\nCO\\nle\\nLO\\nCO\\nxl-\\nIP\\nxf\\nO)\\nCO\\nI s\\nCD\\nCO\\nN\\nCM\\nCO\\nCO\\nrx\\nz\\nle\\nCO\\n\u00e2\u0096\u00a0Yj-\\nCD\\n\u00e2\u0080\u00a2Yt\\nN\\nCO\\no\\np\\no\\n\u00e2\u0096\u00a0M-\\nCM\\ncp\\nCM\\no\\nCD\\nz\\nN\\no\\nXj-\\nCO\\nxf\\nCO CM CM\\nLO -O\\nX H CM\\nr- Cx o co\\nCO CO CM O y\u00e2\u0080\u0094\\nco co\\ncot-cdcolocooolocooo\\nCM CO y- t- O O CO co\\ny- CO K\\nLO\\n\u00e2\u0080\u0099-CMCM T\u00e2\u0080\u0099TCMCJi-OM OKo^CMiOOJOONCoKM\\nM-COCO D ~CO C\\\\jC0 r T T- CM CO CO CO\\nr-mCO^^CM\u00e2\u0080\u0099 r- Y- Y-\\nCO CO\\nxf o-\\n-j O O 7^\\nMMO)C) COCMCM\\nr- i C-i ^M y\u00e2\u0080\u0094\\no o\\nxr 0-\\nIMCOQCOQIOO\u00c2\u00ae\\nCM CM\\nCO I s\\nT ~COCDOOxfCOO-CO\\nT- M- co co CO\\nCO I s\\nCM\\n\u00e2\u0096\u00a0o-\\nT TCMOO)OCOO(OCOO) T(OMOO t c O MCtl\\nrr\\\\ CP\u00c2\u00bb \\\\j- ^T) y-\u00e2\u0080\u0094 Y-. in CT\\\\ t*.\\nMM\u00e2\u0080\u0098COCD (DCOm\\nI-\\nco CO*\\nLO P\\n00 I s\\nCO\\nCO (O P IT) N OHfi\\nCD *0 i\u00e2\u0080\u0094\\nT- O-\\nCo\\nM|M:co ninoco!OM-in fCMa 3 s ooCMOO)\\nS S in C\\\\l m y\u00e2\u0080\u0094 CO O) CO r- i- -7 t\u00e2\u0080\u0094 Cn y\u00e2\u0080\u0094\\nCM\\n\u00e2\u0096\u00a0M-LOCOCO LOCMOO\\n\u00e2\u0080\u00a2r- Y- T- O) CM\\nco co Y\u00e2\u0080\u0094\\nLO\\nCM\\npNcomcocoOiocoNincDCOLrYr\\n(DmYtiniYOiOli-T-YtinmCnSs\\nco\\nCO\\nco\\nCM\\no\\nCp\\nCM\\nco\\nm(D\u00c2\u00aeM: TCOKcOO OCOCOloCOCMoON 0 (DCO l OCO\\nLOCOCO CO |X. y- lo O) co I- T- 7 O CD 00 CM\\nOO y- ?)CM CM LO O y- CM\\nCO co\\nw 3 x x w y\\nTtLococp co 2 in\\nr\\\\i C\\\\i CO C\\\\J\\nCM CM\\nK K-\\n00 00\\nCM\\nTt O\\nCM\\nT- CO CM CM m; oo I y V s; T- Y Y\\nCMCM 7 0 Nl 0 YtY~OD\u00c2\u00abCnD O\\n-CDCD^ i\u00e2\u0080\u0094 Y- Lf 1 CO\\n(D CD\\nuo Co\\nco K co K CO\\nYf\\nLO\\ncm\\n3k \u00c2\u00a3\u00c2\u00a3SS\\nM Yt\\nCOMO)CO CONO)COM NCOLn MM-M:M:CM 3 COCMK( 0 0 (OCM^ NK r T\\nN.CO 0 N 7 p(OM(DOO 73 r-CMCM 7 T-Y (OC 5 cO* ^COO 3 L oCMCO 7 y 77 CO(O^\\ncm T- I s y^- i\u00e2\u0080\u0094 T-_ \u00e2\u0080\u0098y \u00e2\u0080\u0098y CM CM M y\u00e2\u0080\u0094 CM I-\\nco co co cm -r- y~t\\nCM\\nCO\\nco\\nCM CM\\nCO cp CO 2) xD\\nnr CD (O CO CO\\nCD CD\\ncm Cm\\nK co CM CD\\nCM T-\\nK\\ng\\nUJ\\ncri\\n5\\no\\no\\nUJ\\ng\\nCD\\no\\no\\nw\\nCD\\no 0\\nc\\no\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094\\nD\\nJD\\nE\\no\\no\\ntS\\nc\\nl\u00e2\u0080\u0094\\n0\\nc\\n3\\n1\\ni\\no\\no\\nI\\nCD M Jj\\nO CD i:\\no o o o\\nc\\no\\nto\\n3\\n-Q\\nE\\no\\no\\nto\\nc\\na)\\nc\\no\\ns\\no\\no\\nJ\\n03\\n0\\no\\nrzr\\n0\\no\\no\\n0\\n0\\n0\\no3\\nc\\nc\\nc\\no\\no\\no\\n3\\n3\\n3\\n.\u00e2\u0096\u00a0tf\\n,-t^\\nCO\\nCO\\n3\\n_c\\nc\\n_c\\n0\\n3\\n\u00e2\u0080\u0098o\\no\\no\\n0\\n0\\n0\\nE\\nE\\nE\\nE\\nE\\nE\\no\\no\\no\\no\\no\\no\\nCO\\nc\\nid\\n\u00e2\u0096\u00a0g\\nCD\\nCL\\n4\\nCL\\n0)\\no\\nX\\nm\\nII\\no _\\n05\\nif\\n8^\\nay\\n2 CL\\nV)\\n0)\\no\\nJD\\n.1\\nV)\\ns\\no\\nI\\no\\ni\\nco\\nI\\nK\\no\\nQ\\no\\noc\\n0.\\nCL) -J\\n-J\\n6\\n\u00e2\u0096\u00a0S \u00e2\u0080\u0094i\\nc\\n-O y\\nm 5\\ns\\nDC 3;\\no\\nZ222SS^\\ncm cm\\nO)\\n\u00e2\u0096\u00a0Q\\nCD\\ng\\nE\\nQ)\\nsc\\no\\ng\\n\u00e2\u0080\u0098c\\nD 7 r\\nO) CD C\\n\u00e2\u0096\u00a0c\\nu\\n\u00e2\u0096\u00a06\\nCD\\n.y\\n\u00e2\u0096\u00a0Sy-S\\n\u00c2\u00abCJ\\n\u00e2\u0080\u00a2Q\\nc\\nCD\\no\\nc\\n5!\\nCD\\nll\\no o\\nL~\\no\\nc3\\nCD\\nCD\\nCD\\nCD\\na\\nfS\\n-c\\no \u00c2\u00a3M\\n18\\no\\ng 5\\nc\\n03\\na\\nk_\\no\\nc\\nCD\\nCD\\nE\\nCO\\nCD UJ\\nco\\n11\\nCD\\ncd\\nCD o\\na:\\nCD\\nCD\\n3\\ncr\\no\\nCO\\nCD CD\\nCD\\n.Is\\n5. o\\no3\\nCD\\no\\n3 co\\nS 5\\n5\\nJc\\no\\nCD\\nCD\\nI\\nI\\nCD\\nCJ\\nco\\nc\\nS3\\nC 3\\nC- O\\nC c\\nO CD CD\\nCL CL\\n3 t\\nCD CD\\no .c\\no\\nC L-\\nCD\\nCL O\\no\\n-3\\n-Q\\nc\\no\\n\u00e2\u0096\u00a0e\\n3\\nCD\\n-c\\nA-2 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0202.jp2"}, "203": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n\u00e2\u0096\u00a0a\\nD\\n3\\nC\\n\u00e2\u0096\u00a03\\nC\\no\\no\\n0\\nn\\n(D\\nI-\\nr-\\nCD\\nY-\u00c2\u00bb\\n05\\nto\\n\u00e2\u0080\u00a2N\\nU) U\\nCM\\nO\\nIf)\\n05\\nI s\\nLO\\nCO CM\\n00 Co\\nC5\\nr-\\nLO\\nN\\nK\\nto\\nO\\nN\\nto\\nN\\nto\\nto\\nto\\nC\\\\J\\nCO\\nCM\\nCM\\n05\\nlo\\nC\\\\J\\nT\u00e2\u0080\u0094\\nO\\n1\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nY\u00e2\u0080\u0094\\nto\\nCO\\nCO\\nCO\\nto\\nto\\no\\n-r- o\\n5P\\no\\nco O\\nY\u00e2\u0080\u0094\\nto\\nLO\\nCO\\n03\\n05 O\\nLO to\\nO Tl-\\n05\\nCo\\nC\\\\l\\nY to\\nCM\\nCO\\nto\\nto\\nCM\\nY\u00e2\u0080\u0094\\nto\\nCM\\nrj-\\nCO\\no\\n05\\nCM\\nCO\\n05\\nCO\\nCM\\n05\\nto\\n1\u00e2\u0080\u0094\\nCM\\n05\\nCO\\nCO\\nCM\\nto\\nTT\\nto\\nT _\\nY-^\\nO\\no\\n05\\nK\\nY\u00e2\u0080\u0094\\nK\\nCO\\nY\u00e2\u0080\u0094\\nto\\nLO\\n00\\nLO\\n03\\nto\\nco\\nLO\\no\\nCM\\no\\nto\\nSo\\no\\no\\n05\\nK\\nCM\\nY\\nto\\nCM\\nCM\\nK\\nto\\nCM\\nY^\\nY\\nCM\\nCO\\nCO\\n03\\nco\\nY\u00e2\u0080\u0094\\no\\nCD\\ntf)\\nK\\n00\\n00\\n05\\n^r\\nCM\\ni\u00e2\u0080\u0094\\nO\\nto\\nY~-\\nCM\\n05\\nCO\\nCM\\nCM\\nto\\nto\\nCM\\ncm\u00e2\u0080\u0099\\nCO\\nto\\nco\\nY*\u00c2\u00bb\\nO\\nCg\\nCD\\nCO\\nco\\nK\\nY*.\\nY*.\\nY\\nLO\\nY~\\nCM\\ntJ-\\n00\\nK\\nLO\\nY\\n00\\no\\nCO\\no\\np\\nY\\no\\n05\\nCM\\nY\\nto\\neg\\nco\\ntp\\nto\\nCM\\nY^\\nCg\\nCM\\nN\\nCM\\nCM\\nY^-\\n05\\nLO\\nIf)\\nK\\nCM\\nCO\\nO)\\nto\\nCM\\no\\nY*\u00c2\u00ab\\nC^\\n05\\nCO\\nCO\\nco\\nIf)\\nco\\nT\u00e2\u0080\u0094\\ntM\\ncm\\nCM\\nto\\nCM\\nT\u00e2\u0080\u0094\\nO\\nY-^\\nco\\nK\\n05\\nK\\no\\nCD\\nY~\\nLO\\nto\\nCO\\nLO\\nY\\nCO\\no\\n03\\nCO\\ntp\\ntf)\\no\\ntf)\\n03\\n05\\nco\\nY\\nto\\nCO\\nCO\\nY\\nY^\\nY^.\\nY~~\\nco\\nCM\\nK\\nCM\\nTf\\nCO\\nY\u00e2\u0080\u0094\\nY\\nY\\nK\\neg\\n00\\n03\\nCM\\nY\u00e2\u0080\u0094\\no\\nN\\nT-\u00c2\u00bb\\nCM\\n00\\nCo\\nCO\\nto\\nto\\nCO\\nT\u00e2\u0080\u0094\\ncm\\ncm\\nT\u00e2\u0080\u0094\\noo\\nN.\\nO\\nY\u00e2\u0080\u0094\\n00\\nY\u00e2\u0080\u0094\\nY\\nto\\n00\\nY\u00e2\u0080\u0094\\nE 5\\nLO\\nIf)\\nCO\\nTf\\nto\\n05\\nto\\nCO\\no\\nC5\\nY~\\nY\u00e2\u0080\u0094\\no\\nO\\nO)\\nK\\nCO\\nY\\nto\\nCO\\no\\ncp\\ntr\\n1\u00e2\u0080\u0094\\nY^\\nK\\nCM\\nY\\nCM\\nY\\nCD\\nto\\nco\\nCg\\no\\nto\\n-M-\\nCM\\nY--\\nN\\nY^\\nCM\\n05\\nco\\nCO\\nto\\nto\\nCO\\ncm\\ncm\\no\\no\\nCD\\nY\u00e2\u0080\u0094\\no\\nto\\nCO\\nY\\nto\\nY\\nY\u00e2\u0080\u0094\\nY\\nO\\nCO\\nCO\\nY\\nK\\nCO\\nN.\\n00\\no\\nCO\\nK\\nto\\no\\nY\\n03\\nTi\u00c2\u00ac\\nCO\\nY\\nto\\nco\\nto\\n05\\nY\\nT\u00e2\u0080\u0094\\nCM\\nY*\u00c2\u00bb\\nK\\n\u00c2\u00a32\\nCO\\n03\\n00\\nr^\\nK\\n00\\nY-.\\ntf)\\n03\\nto\\nCM\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nto\\nCM\\nY^\\nto\\nCM\\nCg\\nto\\n00\\no\\nDl\\n0)\\no\\n0)\\nu\\ni-\\n3\\nO\\nJOCOOplOpOcoCpCNjlOOCNlOoOOOK^CMCNlooCvjTl-oCO\\n2 YCgtplf)C CglO CMCOCOYCOcMCOCM-yy CO r-\\nY Y T Co CO coco CO Tf\\nO\\no\\nY\\n\u00c2\u00b05 Cg o\\nCg If) CO\\n00\\nOO K CM O\\nT- tf) CO\\n00\\n05\\noo\\nCD\\n00\\nT- CM O CO c\\\\| O O\\no o o\\nCMOO)CMoOi-y-OOC\\nC\\\\|C\\\\| CO^\\nTf C\\\\| CO V) t\\nY C\\\\1 T~ 05\\nK CO ifl\\ny CM\\nC0 OCM O(DOI T\\ny S cm CM\\nCO CO CO co\\n00\\nY O\\nCT\\nCO\\ni\u00c2\u00a35 co r- o\\nQ CO Co 00\\nCO y-\\ny- CM O CD CM o O\\nP^SjOC OWO fCOOO\\nK oo Co CM\\n00 -T-\\nCM\\no o o\\no o o\\nY O\\nY O\\nY O\\nCM\\nCg\\nCM\\nY\\neg\\n03\\neg 00\\nO) o\\nto\\nK\\nCD CO\\nCO Dy\\nO\\nN\\nCM CO O\\nO to\\ntf)\\nto\\nCO Y~\\n00\\nCD\\noo\\nCO\\nCM\\nC5\\nto\\nU0\\nCM\\nCO\\nto\\nCM\\nCM\\n\u00e2\u0096\u00a0Y-\\nY\\nY\\nto\\nK\\nCD\\nCD Y\\nCD\\n00\\n00\\n03\\nO 00\\nO) oo\\nto\\nCD\\n00 y-\\nCO\\nOO\\nCM O\\nO 05\\nY\\nf o\\nCO\\nLO Y~\\n00\\noo\\nto\\nY\\nco\\n05\\nCO\\nY*-\\nY\\neg\\nto\\nto\\nCM\\nCM\\nY-~\\nY\\nY\\nCO\\nNy\\nCD\\nCM\\neg\\nK\\nto\\nCO\\nY 05\\nO) CM\\nY\\nY\\nto Cg\\nt- 03\\nco\\nto\\nCM Y O\\nO Dy\\nto\\nO)\\nCM\\n05\\nC5\\nO\\n05\\nto\\nTf\\no\\nY\\nCM\\nCM\\nCO\\nID\\nto\\nCO\\nCO\\nY\\nY\\nto\\nCO\\nT- O y- O\\no o o\\n(opj\u00e2\u0080\u0099 toocnoo cc no^ g co ^co^ cm\\nt^CMCM^oCQCOM-M-OCO^Oj^CJCO C z Szz\u00c2\u00ae ^PZZ^ZZZZSZZZZZZ\\ncm co y y y cm coco \u00e2\u0096\u00a0^s.^r-co \u00c2\u00abo i-y n\\nCM T- Y~ T-T\\nCM\\nCO\\n00\\n00\\n05\\nto\\nY\\nCo\\nO)\\nO)\\nCM\\nO)\\nO\\nCM\\nT\u00e2\u0080\u0094\\nto\\nYY\\nto\\nU)\\n\u00c2\u00b00_\\nCM\\nT\\nO\\nCM\\nIf)\\nY\\nto\\nR\\nNs\\nz\\nY\u00e2\u0080\u0094\\nCM\\nz\\nCM\\nC)\\no\\nIs\\ni\u00e2\u0080\u0094\\nz\\nJO\\nto\\nZ\\nz\\nO\\nCD\\nCM\\ncm\\ncm\\nto\\nto\\no\\ncg\\nCO\\nSP\\nT~y\\noo\\nC5\\n00\\nto\\nO\\nto\\nto\\n2\\nO)\\nCD\\nY\\nY\\nco\\nto\\no\\ncg_\\nS\\nco\\nz\\nN.\\nY-.\\nz\\nCO\\noo\\nCO\\nT\\nto\\nz\\nz\\nCO\\ncm\\ncm\\ncm\\nY\u00e2\u0080\u0094\\ns s\\nzz^zzzzz\\nCD\\nc\\n\u00e2\u0080\u00980\\noo\\n01\\nO\\nCD\\nc\\nCD\\n0\\no\\no\\n6\\no\\nc\\n5\\ncm\\nCD\\nCD\\n_c\\nCO O\\nCO O\\nO CD\\nCO\\n3\\no w _\\nfc g -O 0\\nC\\n0\\nP -5\\nUJ 2\\n3 J\\nc a o\\no\\no\\nCD\\ne\\n5\\na\\nCD\\n.o\\nc\\no\\nCD\\n3- o\\no O\\nto O) O\\nX\\nx~ co\\nO C\\nO O\\n\u00e2\u0096\u00a0s -e\\n5 2\\nc\\no\\n.3\\nCD\\nc\\ngo _CD\\nCD o\\no\\nc\\n.2\\no\\nLL\\nCD\\n0\\nO CO\\nO CD\\nc\\nCD\\nCL\\nL-\\no\\nc\\nto\\n2\\no\\nul\\ne\\n:3\\nQ\\nQ\\nO UJ\\nUJ I-\\nz 3\\nUj\\nQC\\nto\\n.9\\nu\\nto\\n3\\n03\\n_c\\n\u00e2\u0096\u00a0O\\n0\\n0\\n0\\nQC\\n\u00c2\u00b08\\nto\\n0\\n\u00e2\u0096\u00a02\\nc I\\n.\u00c2\u00a71\\n_c\\nV)\\noa\\n0\\no\\no\\nl\u00e2\u0080\u0094\\nCL\\njn\\ncO\\n0\\nO 0\\n3 C\\n03 L=\\nO 0\\nE\\nw E\\n0 3\\nCD\\n08 P\\nl\\n\u00e2\u0096\u00a0SS\\nC c.\\no 0\\n1_ o rC\\n\u00e2\u0096\u00a04-^ HP O\\n}0\\nUl\\nCO\\nCO\\nUl\\no\\no\\nQC\\nU 0.\\nJ\\n3 s\\no\\nra P\\n1\\n0 J\\nil\\npc\\nCL UJ\\n0 I\\np\\no\\n03\\no 3?\\no\\n03 _\\n0 0\\nCD\\nc\\n-O\\nc\\nk\\nofl\\n-6\\no\\no _\\n0\\n2 5\\n3\\n\u00c2\u00b1J 0\\n3 0\\n0\\nCL\\nCL\\n\u00c2\u00b0S\\n0\\nJO\\n3\\n0.\\no3\\nkj*\\n0\\nQ.\\n0\\n0-\\no3\\nQ.\\n3\\nCL\\no\\n\u00e2\u0096\u00a0O 3\\nO T3\\n2\\nCL\\no\\na\\no\\nI\\n\u00e2\u0080\u00a28\\no\\n0\\nE\\nJ3\\n5\\n-5\\n0\\nE\\n0\\n05\\no -s\\n0 5-\\nw o\\n05 Q.\\n\u00e2\u0096\u00a05 S\\nQ. To\\no\\nQ.\\n0 0\\n0 0\\nsc\\no o\\nW W\\no\\n3\\n-O\\no\\nk_\\nCL\\nu\\n0\\n0\\n0\\n3\\no\\n0\\nc\\n0\\n0\\nQ\\n-a\\n2 2\\n08 CL\\n0 g\\nIT S\\n0\\n3 E\\n-O .9-\\nO o\\nJr c\\nCL LU\\no\\n0 c\\nc O\\nJI -b\\no o\\n0 0\\n2 CD\\n0\\n0\\n0\\n0\\n0\\no\\no\\nfc-\\nC\\nE O\\n9- 0\\n3 o\\ncr -o\\nLU\\nC 0\\nO 3\\n\u00e2\u0096\u00a0E\\n0 0\\n-C C\\nO 0\\nS 0\\nc o\\n0\\n2\\no\\np\\np\\nh-\\n-J\\no\\nCO\\no\\n0 05\\n05 tJ O\\n.9\\n0\\n0\\nQ.O\\n0 2\\nQ O Q\\nc\\nCO\\nCD\\nAppendix A National Emissions (1970 to 1998) A-3\\nSurface Coating\\nOther Industrial\\nNonindustrial\\nSolvent Utilization NEC", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0203.jp2"}, "204": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nTJ\\n0)\\n3\\nC\\nMB\\nc\\no\\no\\n0)\\nJQ\\nCD\\n00\\nO\\n0\\n0\\n0\\n0\\nO\\n0\\nCM\\nq-\\nCO\\nco\\n03\\nCO\\nr-\\nto\\n03\\nCO\\nI\\nCO\\nCM\\n52\\nco\\nCO\\n03\\nco\\n1\\nT\u00e2\u0080\u0094\\n\u00e2\u0080\u00a2l\\nh-\\nC 3\\n\u00e2\u0096\u00a0O\\n0\\n0\\n0\\n03\\nO\\n0\\nCM\\nco\\nM-\\nK\\n03\\nY\\nco\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\ni\\n03\\nCO\\nCO\\n\u00e2\u0096\u00a0o-\\n0\\nCM\\n0\\nCO\\nCM\\n03\\nr\u00c2\u00bb\\n0\\nco\\nr-\\nT\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094\\nco\\nS\u00c2\u00b0\\n0\\n0\\n0\\n00\\nO\\n0\\nCM\\nK\\no-\\nO-\\nK\\n03\\nCO\\n0\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\n03\\nK\\nCO\\nCM\\n0\\nCM\\nco\\nco\\n03\\nO\u00e2\u0080\u0099\\nCO\\ny\u00e2\u0080\u0094\\nre-\\nCO\\nCO\\n0\\n0\\nCO\\nO\\n0\\nCO\\nio\\nCM\\nco\\nCO\\nO\\nY\u00e2\u0080\u0094~\\n03\\n0\\n03\\nCM\\nZ\\neo\\nCO\\nY--\\nC\\\\j\\nCO\\nCM\\nCO\\n03\\nr\u00e2\u0080\u0094\\nCO\\nr\\nT\u00e2\u0080\u0094\\nr-T\\n-cr\\n0\\n0\\nCO\\nO\\n0\\nCO\\ncq\\nr-\\nCO\\nCO\\n1\\nK\\nQ\\n10\\n03\\nCM\\nZ\\nCM\\nCO\\n\u00e2\u0096\u00a0Y\\nCM\\nO-\\nCO\\n10\\n03\\nCM\\nco\\nT\u00e2\u0080\u0094*\\nCO\\nr-~\\nCM\\n0\\nCO\\nO\\n0\\nCM\\nCO\\n1\\nCO\\nM\\nts.\\nC 3\\n03\\n03\\n03\\n03\\nCO\\nCO\\nz\\nz\\n03\\nY^\\n00\\nCM\\n5\\nco\\nCM\\n\u00e2\u0096\u00a0Y\\nI-t\\nY\u00e2\u0080\u0094\\nCM\\nN.\\n0\\n0\\n0\\nCO\\nO\\n0\\nCO\\n00\\nCO\\nCO\\n0\\ny\u00e2\u0080\u0094\\n\u00e2\u0096\u00a0Y\\nSP\\n03\\n03\\nz\\nz\\nco\\nr\u00e2\u0080\u0094\\n0\\nY\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nCM\\n52\\nco\\nCM\\nCO\\nr-\\ny-T\\n1\\nCO\\nCM\\nCM\\n0\\nCO\\nO\\n0\\nCO\\nCM\\nK\\nK\\nO\\nC 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00\\nO)CO M-COC0CMC30C0\\nCM CM W CO\\nY Y T- Y Y\\nY CO CO\\nCo CO CO\\nY \u00c2\u00b0o \u00c2\u00a93 Y y\u00e2\u0080\u0094 y-\\nll- co CO o\\nto CO co\\nCo y-\\nO O CM\\n\u00c2\u00a9NC\\\\|Coo^CO\u00c2\u00a9t-^\u00c2\u00a9C\\\\j\\n\u00c2\u00a90\u00e2\u0080\u0099~03\u00c2\u00a9\u00c2\u00a9\u00e2\u0080\u0099~CM\u00c2\u00a9 r CO\\nM- f\\nh- r-\u00e2\u0080\u0098 03* K 10 T-\\nCO CO CO r-\\nco CM CO\\nCC 3 y\u00e2\u0080\u0094\\nO co\\nCO CM\\nco\\nCM\\nc\\no\\n,c\\n:2\\nY\\nY\\nCO CO\\nY\\nCO\\nO O CM\\nO O O CM O\\nOOO\\nCMCOCOOCOQCOCO\\n0 \u00c2\u00a9K\u00c2\u00a9 03 \u00c2\u00a9CON\\n03\\nCM\\nO 03 co*\\nCO CO CO\\nY K\\nto co co\\nr- cp\\nco N\\nco co\\nco\\nco\\nC 3300 C 3 r^ T |s 03 CMCOCO\\nlOr -O3C0COCOC cOlO\\nco co 10 y_ lo co cq\\n03 03 O 3 Y _ 00 CO Tt T-\\nlo CO CO T-\\n0 -I^. 03 [V^t-QCOa 30 -CpCO\\nK(o\u00c2\u00a9Nt-\u00c2\u00a9\u00c2\u00a9io\u00c2\u00a9\u00c2\u00a9\\nO CM O Cf) M\u00e2\u0080\u0099 CO q\\ncm o o lo oo co lo T- y-\u00e2\u0080\u0098\\n\u00c2\u00a93 Y Y T-\\nco\\no\\nCO\\nCO 03\\nY O\\nCO\\n10 0\\nY\\nCO\\nK\\nCO\\nCO\\nOOOT-0\u00c2\u00b00[^C003COCOCMOtr)03lO\\nO O)\\nCO y\\nnT rC k\\nCO CO CO\\nw y- O b cm\\nCM 00 Y^ q CO CM CM\\nco co co 10 T-\\n2\\nz z z\\no o\\nO K K\\nlo CO Y CO\\nO CM CO\u00c2\u00ac\\nCO cm CM\\nCo Tj O-\\nO tCOtOOJCOCOCO\\nCO O o CO CO CM\\n03 cq CO U3_ co_ cq\\nlo 03 co co 1-\\nK ^r\\nco\\nz z z\\nOOtC0N\u00c2\u00aeC0O fWCMQC0(0\\nC0\u00c2\u00a9\u00c2\u00a9\u00c2\u00a9n\u00c2\u00a9MN\u00c2\u00a9\u00c2\u00a9 cm\\nCO cm O CO CM\\n5 CO\\nto co\\nO\u00e2\u0080\u0099 O\\nr-T 03 K |C\\nCO r\\n03\\n00\\nK\\nco\\nco\\nI 03 03\\nK Tf TJ-\\nCO K\\n\u00e2\u0080\u00a2ct cm\\nCOCOO M IOCO\u00e2\u0080\u0099-IO\\nKKcOCOCM- -COCO\\n03 co cm cm\\n00 K rZ t-\\nCM\\nz z z z z\\n03 T- CM 03\\ns CO oc\\nO 10 CO cm\\nco co q\\nK CO\\nN CM\\nCO 03 CO CO CO\\nT-_ CO_ tq T- T- T~\\nco o co (Z 1\\nZ Z z z z z\\n3\\nO\\nCo 00 CO Cm 0\\nCM O\\n03 03\\nto CO\\ncm r co\\ncootnio\u00c2\u00abr\\nc\u00c2\u00b0 z\\n1 03 03\\n03\\nC3\\nCO\\nto\u00e2\u0080\u0099 03 co is.\\n2 S 3\\nZZzzzzz\u00c2\u00a7g\\nCO CO\\nM- CO\\n00\\nS 52\\nCo co CO\\nO CM CO CM\\nh O CO 1-\\nCO N N\\nco o Co co\u00e2\u0080\u0099\\no\\no\\no\\no\\n_\\nO)\\np\\n_\\nc\\nc\\nc\\nv_\\n.03\\nC\\nE\\nc\\n.\u00e2\u0096\u00a05\\nD\\nCD\\n4\\nE\\nS\\n0\\nu\\nH\\nc\\n0\\nro\\ntd\\n,c\\n-c\\nc O\\nw\\nro\\nz\\nH o\\nO -p\\no.\\nf 0\\nLu\\n-J\\no\\n/3\\ns\\nw\\n-SJ\\nu\\n\u00e2\u0096\u00a05\\n2\\ns\\n03\\nw\\np\\nQ\\ns\\no\\nop\\no z\\no\\nUJ o X q\\nD -s E\\nQ\\n-S, o\\n-95 e\\n03\\no\\n2\\nw\\nCM\\no\\n2\\n\u00e2\u0096\u00a0\u00e2\u0099\u00a6w\\nco\\nCtj\\n0)\\no\\nJZ\\nV)\\n0 0)0\\no\\n3 3 3\\n3 T? -S Q\\n3 il i I W\\n-C -C Z m\\n\u00c2\u00abI\\n03 .W\\nX Q\\n1 s\\ni?\\n2 a -c\\nQ)\\nTo\\ni S 5\\nV 3 3\\nI s 2 2\\n2 S\u00e2\u0080\u0099 ii 1\\nA-4 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0204.jp2"}, "205": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n~a\\nD\\n3\\nC\\n3\\nC\\no\\no\\nI\\n0)\\nn\\n0\\nh-\\nco\\nCM\\nco\\nK\\n00\\nNt\\n05\\nco\\n00\\nCO\\nco\\n0\\nco\\n00\\n05\\nyy\\n1\\n00\\nCO\\nCO\\nM\\nCO\\nCO\\nN.\\nCO\\n00\\nCM\\n05\\n05\\nCO\\nco\\nCO\\nco\\n0\\nM-\\nCO\\nT~-\\nK\\ni\u00e2\u0080\u0094\\nO5\\nCO\\n3\\nco\\nc\\\\T\\nyS\\n1\u00e2\u0080\u0094\\n1\\nn-\\nCO\\nN.\\nF\u00c2\u00b0\\nCO\\n05\\n05\\nco\\nNt\\n05\\nN\\nTj-\\nco\\nCO\\n05\\nYy\\nCO\\n00\\nCO\\nco\\nY\u00e2\u0080\u0094\\nCO\\n05\\nK\\nco\\nLO\\nK\\n05\\nco\\nT\u00e2\u0080\u0094\\n00\\nCO\\nco\\nco\\nNt\\nCO\\nr-\\nCNJ\\nK\\n3\\nK\\n05\\nco\\nc\\\\T\\nCM\\nT_\\nCO\\nCM\\nCO\\nco\\nCO\\nNt\\nCO\\n05\\nK\\nC\\\\J\\nCNJ\\nco\\nNt\\n05\\nCO\\nco\\n05\\n0\\nr -o\\n1\u00e2\u0080\u0094\\nK\\nCO\\n05\\n05\\nCM\\n0\\n00\\nCO\\n10\\nCO\\nt\\nco\\nY~\u00c2\u00bb\\nCNJ_\\nK\\nT_\\n3\\n|C\\n05\\nco\\ncsf\\nCM\\nT\\nin\\nCM\\nCM\\nC5\\nCO\\n05\\n1\\n05\\n05\\nK\\nO)\\nco\\n10\\n05\\nCM\\nCO\\n0\\nNf\\nC5\\nCO\\n05\\nCO\\nCO\\nCO\\n05\\nCM\\n1\u00e2\u0080\u0094\\n00\\nCO\\nCO\\nCO\\nNt\\nNJ-\\nr~-\\nCNJ\\nK\\nr\u00e2\u0080\u0094\\n3\\nK\\n05-\\nco\\nc\\\\T\\nT J\u00e2\u0080\u0098\\nCM\\nT\u00e2\u0080\u0094\\n*r\\nCO\\nin\\nK\\n0\\n05\\nCO\\n05\\nCO\\n00\\nCO\\nco\\nCO\\n05\\nco\\nK\\n0\\nco\\n05\\nCO\\nCO\\nCO\\nco\\nCO\\n0\\n05\\nK\\nr\\nco\\nCO\\nCO\\n0\\nNJ-\\nCO\\nY\u00e2\u0080\u0094\\nCNJ\\nK\\n1\u00e2\u0080\u0094\\n05\\nc 6\\n05\\nco\\ncvj\\no\\nD\\nY-\\nTO\\nu\\n0)\\no\\nk_\\n3\\nO\\nNCOCDO (OP)lOlOCO t\u00e2\u0080\u0099 QC\\\\lirui^ r -C 2\\nnj- co in co to n co o io\\nY~ O) Y- 1\u00e2\u0080\u0094 (v. If)\\nt MO t\\nlOCOCoCOlOCOCD M OOCM\\nCO\\n05 1-\\nf j-toiocMtocoiocri f\\nNJ- Nt N lo lO O\u00e2\u0080\u0099 CO\\n0 1\\nCO\\n00 o\\nP\\n1(0 0)10\\n1- CD o-\\ni- CO lO\\nNf\\nin\\nP\\nf n io o\\n^(0 0(0(0(NN^\\nI*\\n05\\nCNJ\\nK\\nK\\np s\\nCO\\nM t- O\\nr- CO CO CO\\n1\u00e2\u0080\u0094 CD CO i~\\nt o 5 M\\nT- (O O to\\ni\u00e2\u0080\u0094 co 0 i\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nCM\\nNT-\\nC5\\nCM\\nCO\\nCM\\n05\\nCO\\nco\\nYt\\nco\\n05\\nNt\\nN\\nYy\\n05\\nCNJ\\nK\\nO\\nK\\nco\\nNt\\nNJ-\\nco\\nCO\\nO\\nCO\\nCO\\nK\\nin\\nCO\\nco\\nCO\\nCO\\nco\\nNt\\nCM\\nY-.\\nCM\\nN\\nY-y\\n05\\nCD\\nco\\nco\\ncm\\nyS\\nI\u00e2\u0080\u0094\\n05\\nCO\\nCM\\n0\\nin\\nCO\\nCO\\nCO\\n05\\nCO\\nCO\\n05\\nco\\no-\\n0\\nNt\\nP\\n05\\n05\\n00\\n(\u00c2\u00a35\\n0\\n05\\nco\\nco\\nCM\\nin\\nCM\\nCO\\nYY\\nCO\\nCO\\nK\\n0\\n05\\n0\\nCO\\nCO\\nCO\\n0\\nNJ-\\nY~-\\nY*y-\\nNy\\nYY\\nY~*\\nCO\\nCD\\n00\\nco\\ncm\\nn\\nCO\\nYy\\nCM\\nK\\nY-\\nNt\\nO\\nNt\\nC5\\nCO\\nCM\\nYt\\nCO\\n00\\nK\\nCM\\n00\\n00\\npo\\nCO\\nCO\\nO\\nO\\nin\\nCM\\nC5\\nin\\nYy\\nCM\\nCO\\nCo\\nCm\\nCO\\nco\\nNt\\nn\\nh-\\nCO\\nCO\\nK\\nNt\\nNt\\nO\\nco\\nY~\u00c2\u00bb\\n05\\nlo\u00e2\u0080\u009d\\n00\\nco\\nCM\\nTY\u00c2\u00ac\\nY~\\nTf\\nin\\nCO\\nCO\\nK\\nCO\\nN-\\n0\\nO\\nCO\\nK\\nCO\\nCO\\nCM\\n\u00e2\u0096\u00a0M-\\n05\\nco\\nCO\\n05\\nCD\\nco\\nC5\\nco\\nYY\\nK\\nin\\nYy\\nY-y\\n05\\nCO\\nCM\\nCM\\nco\\nNt\\nY-\\nCO\\nCO\\n0\\nK\\nCM\\nY\\nCO\\nY~y-\\no_\\nCO\\nYy\\n1\\neo\\nLO\u00e2\u0080\u009d\\nco\\ncm\\ncm\\n1\\nr_\\n05\\nCO\\nO\\nCO\\nK\\nNt\\nN.\\nO\\nCO\\nCM\\nCM\\nCO\\nN\\n1\\nCO\\nCO\\nNJ\\nN\\nCNJ\\nCM\\nC5\\nNt\\nCM\\n0\\np\\nYy\\n1\\nCO\\nCO\\nCM\\nCM\\nCO\\nNf\\nK\\nO\\nCO\\nCO\\nK\\n05\\n0\\nK\\nY\u00e2\u0080\u0094\\n0\\nCO\\nYy\\nYy\\nK\\nID\u00e2\u0080\u009d\\nCO\\ncm\\ncm\\nT-\\n1\\n1\\nCO\\nO\\nCO\\nCO\\nK\\n00\\nco\\nYy\\nCO\\nO\\nCO\\nCO\\nin\\nCO\\nYy\\n05\\nCO\\n0\\np\\no-\\nCO\\nY--\\n0\\nin\\nO\\n0\\nCO\\nNT\\nY\u00c2\u00bb\\n0\\nCM\\nYy\\nYy\\nCM\\nCO\\nNt\\nCO\\nCD\\nCO\\nCO\\nK\\n00\\nCO\\nCO\\nY\u00e2\u0080\u0094\\n0\\nCO\\nYy\\nYy\\nnT\\nO\u00e2\u0080\u0099\\nNT\\ncm\\ncm\\nT-\\nr\\nT\\n05\\nCT)\\nCM\\nCO\\nK\\nCO\\nN\\nCO\\nY--\\nC5\\nin\\nC)\\nO\\nCO\\nNt\\nin\\nNt\\nNJ-\\n05\\nLO\\nY\u00e2\u0080\u0094\\n0\\nO\\nco\\nCO\\nCO\\nYy\\n05\\nO\\nCO\\n0\\nY\u00e2\u0080\u0094\\nNt\\nCO\\n05\\nCD\\nco\\nCO\\nCO\\n1\\nCO\\nCM\\n0\\n05\\nin\\nYY\\nYy\\nin\\nco\u00e2\u0080\u009d\\nkT\\ncm\\ncm\\nY-\\nT-\\n05\\nO\\n05\\nK\\n05\\nNt\\nco\\nn\\n00\\n05\\n0\\n05\\nCM\\np\\nCO\\nCO\\nCO\\nCO\\nCD\\n05\\nCM\\np\\nco\\n05\\nCM\\n05\\nCM\\nK\\nCO\\nY\u00e2\u0080\u0094\\nK\\np\\nn\\nCM\\nin\\nK\\nK\\nCO\\n0\\n05\\n00\\n0\\nYY\\n\u00e2\u0096\u00a0O-\\nCNj\u00e2\u0080\u009d\\nco\\ncm\\nYy\\nY-\\nT\\n05\\nCO\\n0\\nCO\\nNt\\nK\\nK\\nCO\\n00\\np\\nO\\nCM\\np\\nCM\\n00\\nK\\nO\\nLO\\nCO\\n05\\nCO\\nCM\\nCO\\n05\\nCM\\nK\\nm\\nCO\\nCO\\nY^\\nCO\\nP\\nYy\\nI s\\nCM\\nco\\nin\\nCO\\nCM\\n05.\\nco\\nco\\n1Y\\nco\\nvS\\nco\\nY\u00e2\u0080\u0094\\nYy\\nY\u00e2\u0080\u0094\\nT\\nO\\nCD\\nCO\\nco\\nin\\n05\\nCM\\nin\\n0\\nCO\\n\u00e2\u0080\u00a2u:\\nCO\\n0\\nY^\\nNt\\nCO\\nco\\nCO\\n05\\nN.\\np\\nin\\nco\\n05\\n0\\n0\\nY~-\\n2\\nIP\\nco\\n00\\nYy\\nP\\n05\\n0)\\nCM\\nco\\nin\\nCO\\nCM\\n05\\nK\\nYt\\nCM\\ny\u00e2\u0080\u0094N\\ncT\\nin\\nYy\\n1\\nC\\\\| CO CO Co Y\\nCO CO\\nMo c\\\\|\\nin\\n1- CNJ\\n05 T-\\n(O CO\\nO CM\\n05 T-\\nco \u00c2\u00ab5 CM CM CO it\\nK i\u00e2\u0080\u0094 CO i\u00e2\u0080\u0094\\nNt CO CM CM CO O\\nK y- CO CM\\nCO i\u00e2\u0080\u0094\\nCO CO\\nNt O\\nCO CO\\nK lO CM\\nCO\\ni- CM\\nO CO\\n05 i-\\nCO Nt\\np5CMCMCOlOi-CMC35\\nK i- CO CM 05 N}- Nt\\ni\u00e2\u0080\u0094 m Nf t-\\nCO M-CM M-oOCO M-CO\\nCO CO CO 00\\nco i-\\nCM CO O CO O Co\\nCO CM CO CM Nt\\ni- in Nt i-\\nY CM\\n00 co CM\\nCO\\nCO\\nNf if 05\\nO CM\\n05 T-\\nNJ- O\\nCO\\nin co fs co\\nin 05 05\\n05\\n1- CM 0 M\\nCO 05 co\\n05\\ni\u00e2\u0080\u0094 cm i\u00e2\u0080\u0094 i\u00e2\u0080\u0094 in co in.\\nT CO CM Tt 05 Nt\\ni- in co\\nCM T- CM CO CO\\nCMCMtNNf\\ni- m co\\ncm m; co 05\\n05 CO\\nco\\nco\\no-\\nCM\\nCO 1- CO CO K\\nCO N CO\\nco\\n5\\nCO CM\\nTt CO\\nh-\\nK\\nCO\\nc r to o 0 c\\\\i\\no n cp\\nc 4 1- t CM\\nCD O\\n05\\n00\\nCO\\nNt\\nth:ococm!POh j:no c i:\\nO W CM 5 Z\\nr r co co cm\\no CM CM\\nin\\no C in o j;\\no 5 5\\nUj\\n-J\\no\\n5\\nQ\\n2:\\nfo\\nUj\\n3\\n2:\\nUJ\\nQ\\no\\nQC\\nI\\no\\n2\\nCD\\n_c\\no\\nc/5\\nCD CD\\n.2\\nffl 5\\nc\\n05\\nC TO\\n.o s\\n\u00e2\u0096\u00a0a_ cd\\nO .CD 05\\n2 *s\\nS c\\n-6\\n8-2-2\\n0\\n1\\nCD\\n2\\n2\\no\\no\\nJo a\u00c2\u00bb\\n.c\\nCD\\n2\\nCD\\n.o\\ns\\nCD\\nOlw x\\n\u00c2\u00a7.e-\\n-2 CD\\n\u00e2\u0080\u00a22\\nCD\\nc/5\\nw\\ng\\nD\\nO (D\\nc c\\nCD\\nc\\nCD\\nCD\\n2\\nCD\\nC/5\\n05 CD\\nCD\\n.1 Q\\ny ~Q\\nS 0 cp\\nCD 25\\nz\\nc\\nI\\nCD\\nc\\no\\no Id 05\\n2 S oa\\nO E P\\n2 8 -2 -2\\nCD\\n2\\nCD\\n2\\n2\\no\\no _\\n2 5 2\\nCD E o\\n\u00e2\u0096\u00a02\\nCD\\nCO\\nCO\\nCD\\nCD\\nO CD\\nC C\\n2 c\\nC CD\\nCD o C\\n\u00e2\u0096\u00a08 -2\\n2 c\\n8 5 .2\\n.ct o 2\\njfi\\n0\\n0\\nO) S-tt: u id C s ID\\nIf2 S 8s S\\nCD\\nc\\nv. -O\\nCD CD\\n-c o\\n2 CD\\n2\\ncd a 3\\n0)0\\nCD\\na:\\n10\\nco 2.\\nCD 3)\\n3 -2\\ns\\nO\\nCD CD\\nQ- 8\\nS3\\no C y.\\ncr 3\\nCD\\n-C\\nC a\\no\\n8\\nAppendix A National Emissions (1970 to 1998) A-5", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0205.jp2"}, "206": {"fulltext": "National Air Pollutant Emission Trends 1900-1998\\n~o\\nD\\n3\\nC\\n\u00e2\u0096\u00a0M\\n4-\\nc\\no\\no\\n0\\nn\\nCO\\nco\\nr- O) O O\\n03\\nCM y\u00e2\u0080\u0094 7\\nLO\\n03\\n03 03\\n0\\ni\u00e2\u0080\u0094\\n00 co\\nd\\n00\\nr-\\ntcoo\\no\\n03\\nCO CO 7\\nO)\\nr- t-\\ncm cm\\n0\\nY\u00e2\u0080\u0094 1\u00e2\u0080\u0094\\n03\\nCO\\nT- 0 O O\\n03\\n03\\nMr 7 z\\nr^-\\n03\\nI\u00e2\u0080\u0094 T\u00e2\u0080\u0094\\nt\\nT\u00e2\u0080\u0094\\nY- T-\\nto\\nY-~ T\u00e2\u0080\u0094\\n03\\nin\\nOO 00 o o\\nCO\\n03\\n03\\nJ 7 O) z\\nC\\\\| CM\\nLO\\nCO\\nNT rd\\nco\\n03\\n\u00e2\u0080\u00a2cf\\nCO CO o o\\nCO\\n03\\n03\\nJO 7 CD 7\\nCO CO\\n0\\nco\\n03 03\\ncm\\no\\nY\u00e2\u0080\u0094\\n00\\nCM CM O\\no\\n03\\n03\\n\u00c2\u00a7Z\u00c2\u00ae2Z\\nCO\\n1\\nT\u00e2\u0080\u009c\\nNT id\\ncd\\n03\\nCM\\n3 o o\\no\\n03\\n03\\nco 7 CO 7\\n03 03\\n00\\nco\\ncd co\\nid\\n03\\noo CO o o\\nCM\\n03\\n03\\n25 _z\\nco\\nco co\\nd\\no\\nT_\\nO\\nCM CM O O\\nCO\\n03\\n03\\n52 z z\\nCM\\nCO\\nY-*\u00c2\u00bb y\u00e2\u0080\u0094\\nco\\ny\u00e2\u0080\u0094 T\u00e2\u0080\u0094\\n03\\n03\\nCO CO\\n03\\nCO\\n03\\n2 z 5 z z z\\nCO\\nT\\noo oo\\nco\\no\\nT_\\noo\\nJO to\\n03\\noo\\n03\\n\u00c2\u00a7zgzzz\\nCM\\nh-\\nCo in\\nco\\nY\u00e2\u0080\u009c- T-\\nT\u00e2\u0080\u0094\\nT\\nCO\\nr*.\\n00\\noo\\n03\\nCM 7 CM 7 7 z\\n03 03\\n1\\no\\nY\u00e2\u0080\u009c\\nfs. fd\\nrd\\nT\u00e2\u0080\u0094\\nT\\no\\n2\\n\u00e2\u0096\u00a0^r\\noo\\n03\\nj 7 M\u00e2\u0080\u0099 7 T 7\\nco\\nod oo\\nid\\nY\u00e2\u0080\u009d\\ny\u00e2\u0080\u0094\\nIC3\\nco CO\\nr~\\n03\\nCp z CO z z Z\\nC\\\\j c\\\\J\\nLO\\nO\\nY\u00e2\u0080\u0094\\nIfT LO\\nco\\nY\u00e2\u0080\u0094\\n-r-\\no\\na 03\\n1\\n03\\nJ5 7 O 7 7 z\\n03 03\\n0\\nrd id\\n03\\nCM\\nY\u00e2\u0080\u0094\\nCO\\nS)\\nLU\\nc\\nO\\n(fl J: O\\ncc\\nS ,9 m\\nLL (fl 0 SI!\\nD\\no\\nUj .q 0 g 0\\no\\no\\n0\\n0\\nY-Y\\n0\\no\\n2 E 8 ,2 o\\n33o\u00e2\u0080\u009d\u00c2\u00bb?\\n.J O -C C\\n_i\\n_j\\n0\\n0\\nk_\\nIn O\\n-c 0 o a\\nO 03 5= 0 o\\n0\\nW O I O 1 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k_\\n3 0 0\\no\\n-0 o\\nc\\no\\no\\n4\u00e2\u0080\u0094\u00e2\u0080\u0099\\n0\\n5 -c e\\n2\\no S\\nc 0\\nII C\\nZ\\n52\\n0\\no\\n0\\n0\\n03\\n0\\no\\n0\\nF\\nO\\n03\\n0\\nLO\\n03\\nr\u00e2\u0080\u0094\\nC\\no\\nk_\\n0\\n4\u00e2\u0080\u0094\\n\u00e2\u0080\u00990\\nsz\\n0\\n4\u00e2\u0080\u0094\u00e2\u0080\u0099\\nC\\n4\u00e2\u0080\u0094\\nC\\no\\no\\n0\\n0\\n0\\nO\\n*0\\n0\\n0\\nc\\nE\\nE\\n0\\n0\\n0\\n0\\nk_\\n-c\\n0\\n*k-\\nCL\\no\\n0\\nc\\nO)\\nk_\\no\\n0\\n0\\no\\n0\\n0\\no\\no\\n3\\n0\\nk~_\\n0\\n0\\n\u00e2\u0080\u00a2O\\n.c\\n2\\nk_\\no\\np\\nN\\nc\\nA-6 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0206.jp2"}, "207": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nC\\no\\n0 o\\n-O 4-\\nX\\no\\nc\\n0\\nU)\\no\\nc\\\\i\\nl\\no\\n\u00e2\u0080\u00a2C\\nT3\\nC\\n05\\n3\\nO\\nx:\\n0\\n-Q\\n3 m cm o cm\\no O) (M If)\\ns~ CO Co 1-0 C \\\\1\\no U) p) T-\\n^CO(OC\\\\J r^(MOij(OO c0(O^0Cl\\noo st 3 m co 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CM CM\\nlx\\nO\\n05\\nY-x\\nY-x\\nsq;\\nSt\\nCO\\nCM\\nCO\\nCD\\nlx\\nLO\\nC3\\n05\\n00\\nsq;\\nX\\n12\\nCD\\nCD\\nID\\no\\nCM\\nCD\\nCO\\n3\\nz\\n3\\n3\\nCM\\nLD\\n12\\nCD\\nY-x\\nY-x\\nL0\\nS\\nLD\\nCD\\n00\\nX\\nYx\\nY\u00e2\u0080\u0094\\nLO\\noo\\n05\\n\u00c2\u00a35\\nco\\nST\\nY-x\\nsT\\nC3\\nt-\\n2\\nST\\nZ\\nfc\\nCD\\nCM\\nz\\nCO\\nst\\nY-x\\nY-x\\nsr\\nCM\\nLO\\nsf\\ncm\\ncm\\nID\\nCM\\nIP\\nsq;\\nCM\\n25\\nsq;\\nO\\nCO\\nsq;\\nCM\\n5N\\nsq;\\nO\\nco\\nCD\\nO\\nO\\n05\\n00\\nCM\\nz\\nCD\\nlx\\nS\\nCD\\nLO\\nco\\nY-x\\nIX\\nZ\\nCD\\nCD\\n2N\\nCM\\no\\nY-x\\n2\\nCD\\no_\\nZ\\nCD\\no\\nY--\\n5\\nco\\nz\\n52\\n00\\nCM\\nCM\\nCM\\nz\\nCD\\nsr\\nY-x\\nYx\\nK\\nsf\\ncd\\ncd\\nO\\nCT|\\n05\\n4\u00e2\u0080\u0094*\\nC0\\no\\nCD\\nO\\ni\u00e2\u0080\u0094\\n3\\no\\n05\\nC\\nco .2\\n3\\nO os\\n5\\nS\\n5\\n_ .3-\u00c2\u00a7l\\nco -Q 0 cm\\nO\\nO\\nw\\n3\\no\\nc\\nl_\\n05\\n-c\\nCM\\n3\\n;o\\nw\\n5\\n05\\n5\\n05\\n\u00e2\u0096\u00a0Q\\nv.\\n05\\n-C\\nC/5\\n(0\\n0\\n3\\ng\u00c2\u00a3\\n.2 co\\n05 5\\na Q\\no\\n05\\nC\\n.05\\nCM O\\nOij\\nUl O\\nu.\\nOQ\\nC/5\\n3\\nO\\nc\\n\u00c2\u00b0a\\n05\\na\\no\\nla\\nI o\\n5-si\\n-Q 0 cm\\ncc\\n;o\\n1 X\\na\\nV)\\nQ) i.\\n05\\nS 0\\n3\\nO Q)\\nS5\\n2\\n.52\\nc5\\n2\\nO\\n3 O\\nW C\\na o\\nCM\\nCD\\n05\\n1\\n\u00e2\u0080\u00a2E\\nCM\\nO\\n1\\n05\\nCD\\nIf\\nC\\no\\nw\\n3\\nD5\\nE\\nO\\nO\\ncc\\nO\\n-I\\no\\no\\nI\\nCO\\nCO\\no\\n03\\nO\\no\\nO\\nIB\\nIB\\nIB\\nc\\nc\\nc\\no\\no\\no\\n3\\n3\\n3\\n^ZL\\nCO\\nCO\\nCD\\nc\\nc\\nC\\n03\\n03\\n03\\no\\nO\\nO\\na3\\nO\\nc3\\nE\\nE\\nE\\nE\\nE\\nE\\no\\no\\no\\nO\\nO\\nO\\n03\\nc\\n05\\n\u00e2\u0096\u00a0g\\n\u00e2\u0080\u0098c/5\\n05\\nCC\\nCL\\n05\\nO\\nX\\nUJ\\nJD\\nE\\no\\no\\n05\\n3\\nT3\\nO\\nO\\nCD\\n_ o\\nCM cm\\nD\\nO CM\\nO)\\n05\\nSx.\\n-2\\n5n\\n6\\nL\u00e2\u0080\u0094\\n05\\n-C\\nAppendix A National Emissions (1970 to 1998) A-7", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0207.jp2"}, "208": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n\u00e2\u0096\u00a0a\\nQ)\\n3\\nC\\nmmm\\nC\\no\\nO\\nCM\\n0)\\nn\\no\\nI-\\no\\no\\n0)\\nTJ\\nO\\na)\\no\\nk.\\n3\\no\\n0\\n^owwtMooNtOt-^n^cowNiOinT-Tfooo wconoon^O -owooo\\nio cm r^- m co r*. co oo t O oo o t-\\nCO\\noiow\u00c2\u00abooO fn oro tN^WT-noo\u00e2\u0080\u0099 ^conoon( iO -owooo\\nt\\\\i in co n co oo -m- o co o Co co io\\nr- rj- CO r\\noomc\\\\io)oooc)ooco tin\u00c2\u00abN(0 fi-oofflJ\\\\i ll o t o\u00c2\u00aboowC iO -o\u00c2\u00abooo\\nCM CO LOCOi-r^ CO CO CO CO OOKCOCO T-\\nt\u00e2\u0080\u0094 r~ CO CM\\nCOOS^ JOO^CONO^OoOCOinClCDOfflONp^WNOOOCOO\\niocm I s in C) i\u00e2\u0080\u0094 co in o oo ra cn co o i\u00e2\u0080\u0094\\nv- CO\\nOo(omiooo t onn f^coroinonoo)o -oco t0ooffl io\\nCO CM N- in J) 1 N 1- CO CO 00 CO co CO co\\noo CM\\nO OJ o o o\\nO C\\\\J o o o\\nl io)inifl^oo--5aiN^poo)inp^O(DON^ fpnoo(!)CiO -oNoo\\nco i- r\u00c2\u00bb locot-cocnji^tj-k oo to f o co\\nCO CM r\\n\u00c2\u00abNoco(Dooo!;nNfflCOfflcD }^no(Ooo)9 ONOOOC)0 -owoo\\nCo CM r~~ in CO r- CD Cf CO N Co CO in CO CO CO T- 7\\nf* CO CM\\nl nwwcoNooco!Oin(oin inwM!Nnocooffl^c))CHMOooC io -oNOO\\nlo W T- N K T- n CNlCDlO CO CO co CO CO r- -7\\nCO CM\\nCOCO(M(OOOOOlN^fCO(Dp)^hCO?lnOr-00^0) 0000\u00e2\u0080\u0099 OOOr-00\\nco i\u00e2\u0080\u0094 i\u00e2\u0080\u0094 oo n o m aoi^-coioco t-\\nT- T~ T- CO CM r\\ncowcocoNooroi5in tM!cNO)r- *inoNoo f l O\u00e2\u0080\u0099 oNCooo wo\\nt- cm m cocoi-iOT-ojTtTt r~ cm cm M- *-o\\nN\\njuvooni-ooo^innnjffli-\\nM-co^ini-o^m\\ncm t-\\n^NCMoinooootccocon^roin\\nCO CO CM CM COCOT-lOr-CMCDin\\nCM T-\\nCO\\nCM\\nt oioocoomcoiococM or ~cooo CMO\\nr- N CM CM M- CO 2 Z Z Z\\nCO CM -r\\ninOCOOCT)KCOO-CM OCOCMOO CMO\\ncm r^coco M-io^\\nCo CM\\nCO-M-cn JO LO CM CM l O M- T-COCOCO T\\nr ^^77777 0 7 ^7 K 7N7977CM7COCr) OlM zzzz 2z2777\\n?t ZZZ2 \u00e2\u0080\u009cZ\u00c2\u00aeZ Z^Z fi i\\n\u00c2\u00bb~COCO CO CO CO CO CM 00 M-CJ)COCO\\nCNjinco 2ZZ22 N 2 i^ 2 co 2 co z eo zz z cocoiocM ZZZZ 5 22Z ZZ22\\n-o- K r- o o K co OTKg^ s\\n077777 7 7 7 7 77 7 0 17777^7777777\\nCM CM\\nO)\\n0)\\nE\\nCO\\nc\\nO) LU\\nCD\\nfl\\n03 o\\nc E\\nE a)\\no sz\\n-c o\\no O\\n.2 c\\nc CO\\nCO O)\\nS\u00c2\u00bb o\\nO\\ncn co\\nO\\nE\\n0)\\n-C\\no\\nC)\\na o) a?\\nSo 3\\n\u00c2\u00b03 5 E\\n3\\nu\\n0\\nE\\nC O)\\nCL\\no\\nE\\nd\\n_ .c\\no\\nc\\nJO\\nsz\\nCL O\\nCO\\nsS\\no\\no\\noc\\na.\\n-J\\n5\\n5\\nCD\\nc\\n\u00e2\u0080\u0098co\\ncn\\nCD\\no\\no\\nCO\\nCD\\n_C\\nCO\\nO\\nCO\\n0\\nLU\\n0\\nZ\\n0\\nL_\\nCD\\n0\\nC\\nif)\\nif)\\n03\\n0\\nO\\nO\\nu_\\nCO\\nCL\\n3\\njf)\\nO\\nL_\\nl\u00e2\u0080\u0094\\nQ)\\ns\\nLi.\\n2\\nUJ\\n8\\nQ\\nUj\\ncc\\nI\\nUj\\n~1\\no\\nUJ\\n0.\\nif)\\na\\n*c\\nif)\\n3\\n\u00e2\u0096\u00a0O\\nc\\n\u00e2\u0096\u00a0O\\na)\\nCD\\ncc\\n\u00c2\u00b0s\\na)\\nO CD\\n3 C\\nO CD\\nQl DC\\nCO E\\nCO 3\\nCD\\n*5 2\\n5 l\\nin\\nUl\\n0\\nfO\\n8\\no\\ncn tt\\n2 U.\\n1*\\no\\n45\\nS\\nc\\n03\\niJ)\\nO\\n3\\nTD\\nO\\nL_\\nCL\\na5\\nU)\\no\\n3\\n\u00e2\u0080\u009cO\\nO\\n03\\n5\\n3\\nCL\\n03\\n-c Qc\\no\\n^3 0)\\n3\\nO\\ni.\\ncn\\nCO\\na.\\nQ. \u00c2\u00b00\\nk.-\\nD\\n\u00c2\u00b00 Q.\\no\\ni 08\\nD\\n_l 3\\ncn- 11\\no\\n3\\nO\\nO\\nL_\\nCL\\nO\\nto\\nCO\\nc/\\n3\\nO\\nCD\\nc\\nCO\\n1 j2\\no o\\nco 3\\nTD\\nO\\n\u00e2\u0080\u00a2U\\no\\no\\no3 CL\\na5 co\\n-Q\\nCD\\n5 \u00c2\u00ab8\\nc s\\nI So\\nis\\no cn o\\ncr i\\n\u00c2\u00abs\\nE\\n\u00e2\u0096\u00a0o .9-\\no 3\\n\u00e2\u0096\u00a1I (S\u00e2\u0080\u0099\\n.9\\nS\\n-5\\nco a\\nm\\nco\\nCD\\nCO\\nCO\\nCD\\nO\\nO\\nc i\\nE I\\n.9- co\\n3\\ncr 7\\nhi c\\nc co\\nO 3\\n\u00e2\u0096\u00a03 0\\nCO CD\\nt c\\nO CO\\nQ.\\nCO CD\\nC O\\nco .2\\nO\\n-1\\nK\\n1\\n-J\\nO\\nCO\\ncn _\\nc co\\nco\\ncn -e\\n.2\\ng .9 S\\n5\u00c2\u00b0 -S.O\\ng to\\n.2 o\\n2 O\\nO\\nLU\\nc\\no\\nCD\\nO\\n_ _ CO\\ncn co \u00e2\u0096\u00a0s.Cr\\nQ k c 3 k\\nQ CD O CO O\\nto -2 M\\n3\\nTD\\nC\\n(1)\\ng\\nc\\n2 05\\nc\\no o\\nZ CO\\nA-8 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0208.jp2"}, "209": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nTJ\\nD\\nc\\nc\\no\\nCM\\nI\\nG)\\nn\\no\\no\\ncl\\n0)\\nTO\\nO\\n0\\no\\nk.\\n3\\no\\nC/3\\nOOOOtJ-oOCVjKt-tJ-oOO\\nO) to M-\\nK T-\\nOC5OO7OOCMtooC0OOO\\nP ito 7\\n^(J)Nt\\\\|NC\\\\|lJ)n OC)(\\\\| fOO) OlO T ONKC)OOC^\\n\u00c2\u00ab3Tt2\u00e2\u0080\u0099 T-P5\u00c2\u00aeC\\\\lN^\u00e2\u0080\u0099 COCOin to CM 7\\nfs co oo on 17 co o to cm\\nnT cm\u00e2\u0080\u0099 cm t- cm\u00e2\u0080\u0099 cm\u00e2\u0080\u0099 io\\nC\\\\| N J Q Q Q C\\\\|\\nto CM 7\\nOOOO7C5OCMtoOC0OOO\\nO) U) M\\n0t 00 ;0700\u00e2\u0080\u0099\u00e2\u0080\u0094 PC07000\\n7 P tO Tf\\ntoT-oo ocoooo7in7ooo\\n2t co 7\\n10t-oO C0OOOC077OOO\\n7 7 CM N M-\\ntoY-oo cooooto-r-coooo\\n7 7 O) U3 M\\nCOr-CMO CMOOOl\u00c2\u00a3lT-cOOOOO\\n7 7 P in 7\\nCM\\nCOOCMO OOOOI~a)CMOOOO\\n7 7 P 7 7\\nc m t-o i- Ot-2t-cm o\\n2 2 z Z n in 2 z Z\\nCM T-0 T- 01-COT-Tt 0\\n7 77 7 CO CO to 7 7 7\\nCM T-0 OObNO) 0\\n7 77 7 CM W 7 7 7\\nI I\\nII\\nr;r7^-\\nZZZZZZZZvI^^ZZZZ\\nP COCO\\nz z z z\\nto to O\\nI z\\nZZZZZZZZ^^COZZZZ\\n\u00e2\u0096\u00a0c\\na) O\\nCD 9-\\n2 g\\no 0\\nCO H\\nK\\ncc\\no\\nI\\n1\\nLu\\no\\n2\\ns\\nco\\nc n\\nc\\njo\\nCL\\nc-3\\nn\\nCO\\nc\\nI\\n3\\nCO\\no\\n3\\nTO\\no\\nk.\\nQ.\\nE\\n3\\na\\no\\no\\n3\\n\u00e2\u0096\u00a0O\\no\\n0.\\nE\\n3\\n0\\no\\nd a)\\nO) CD\\nco co\\nt:\\na) o\\nco 9-\\n2 w\\nO CO\\nCO\\nq o CO CO _\\n0}\\nQ.\\n03\\nE\\n3\\n_0\\no\\nk\u00e2\u0080\u0094\\n0\\nQ.\\nC/5 CO\\nc c\\n.2 .2\\n0 0\\n0) CO\\no 0\\n2 2\\n0 0\\nCO CO\\n0 0\\n2 2\\nE E\\n0 0\\no o\\no o\\n2 2\\nc c\\n0 0\\nO) 05\\n6 6\\nC5\\n0 (J\\ng\\n2 O\\nO 0 Uj\\nCO rat\\n0 o\\no 2 \u00c2\u00abj\\n1 co\\n0 w CO\\nO D\\n.2 2 to\\nr~ ^3\\n0 Q\\nO)^ Uj\\na)\\nas\\na)\\nGO\\n0\\n0\\no\\nCO\\nCM\\nCO\\n1\u00c2\u00b0\\nO\\nCM\\nCO\\nY-.\\ncm\\n7\\nCD\\nco\\nr-*\\nin\\nin\\no\\nCO\\nin\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nCO\\nto\\n05\\n05\\n05\\n00\\nco\\nco\\nCO\\nCM\\nT\u00e2\u0080\u0094\\ncm\\ncm\\nT\u00e2\u0080\u0094\\nCM\\ncm\\nto\\n05\\nK\\nCM\\no\\n7\\nO)\\n7\\nCO\\nto\\nN.\\nC\\\\J\\nr-\\nY\u00e2\u0080\u0094\\nin\\nin\\nP\\nCM\\nO)\\n7\\nr~-\\nto\\nto\\nCO\\n05\\n05\\n05\\nT\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nN\\nCO\\nin\\nto\\ncm\u00e2\u0080\u0099\\ncm\\nr\u00e2\u0080\u0094\\ncm\u00e2\u0080\u0099\\ncm\\nto\\n7\\nco\\no\\nCM\\nK\\nCM\\ni\u00e2\u0080\u0094\\nCM\\nC5\\np\\nto\\nh-\\n7\\nco\\nT-\\nCM\\nQ\\nCO\\nCO\\n00\\nco\\nCM\\nC\\\\J\\n7\\n7\\nin\\n05\\nto\\nCO\\nin\\n7\\nY-\\nco\\nco\\n7\\ncm\u00e2\u0080\u0099\\ncm\\nlf)\\nCO\\nO\\nco\\nh-\\nO\\nK\\n7\\nco\\nC3\\nto\\nto\\nCD\\nN-\\nCO\\nr\u00e2\u0080\u0094\\nin\\nto\\nP\\nin\\nO)\\n7\\nco\\nCM\\nLO\\nif)\\nco_\\n05\\nCO\\nCO\\n7\\n7\\no\\nco\\nco\\nT\\ncm\u00e2\u0080\u0099\\ncm\\nto\\no\\nco\\nCM\\no\\nCO\\nin\\no\\nCO\\nCO\\nP\\nCM\\nrj-\\nco\\nCO\\nCM\\nCM\\np\\nY~\\n05\\n7\\nco\\n7\\nCM\\nCO\\nCO\\n7\\nCO\\nto\\nco\\nCO\\nP\\nP\\nco\u00e2\u0080\u0099\\nco\\nT_\\ncm\\ncm\\n7\\n7\\nC\\\\J\\nCO\\n7\\nco\\nin\\n00\\nCO\\np\\n7\\nCO\\no\\nY*\u00c2\u00bb\\nm\\nco\\no\\n7\\np\\nCO\\nco\\nCM\\n5\\nCO\\noo_\\nK\\nin\\nCO\\nCO\\nCM\\nP\\nco\\nco\\n7\\ncm\u00e2\u0080\u0099\\nCm\\n7\\n7\\nco\\nY-\u00c2\u00bb\\n05\\nN\\nCO\\n05\\n7\\n00\\n17\\nO\\nCO\\nlo\\nr-\u00c2\u00bb\\nCO\\nto\\nCM\\nCO\\np\\nCO\\nto\\nCM\\n7\\n7\\nCO\\nK\\nto\\nCO\\nCO\\nCM\\nP\\nco\u00e2\u0080\u0099\\nco\\nT-\\ncm\\ncm\\n7\\nco co o o o\\nQ CO Co o o o r-\\n7 i~- 7\\nCO CO K o O O T~\\nCO 7\\nCO\\nCO JCmKCOCOOOO\u00e2\u0080\u0099\\nT- co T~ 7\\n00)OCOCM(D^CMCONOKO)M OCO fCMCOCOlflO\\nOOCMO ~lOpoKcMC\u00c2\u00bb M- CO O CM t-CO y-\\nO CM_ CM_ CM 7 7 CO CM CM^ P y-\\nNT co\u00e2\u0080\u0099 CO* t-\u00e2\u0080\u0099 cm cm\u00e2\u0080\u0099 7\\no P 7 to\\nCO CD CO\\n0 7 7\\nNT co\u00e2\u0080\u0099 co\\nCOC07COCOtof7lOP7\\n00 to CO 7 tf) to CM r\u00e2\u0080\u0094\\n0 CO lo 0 M M lo 1-\\nT-\u00e2\u0080\u0099 cm\u00e2\u0080\u0099 cm\u00e2\u0080\u0099 7\\nO\u00c2\u00bb O S J) J l O(D(OCoK0 fCM\\nOO C\u00e2\u0080\u0099 -Ci|O)0OCO COOt-\\nco iq 7^ 7 00 LO CO 7 C0_ 7 t-\\nNT co\u00e2\u0080\u0099 co t- cm\u00e2\u0080\u0099 Cm 7\\nOO1CDNO)oCO0O0C)COQOO)OO\\n5 O O) CO CM p CO CM 00 CM CO o\\nto co 0 O) 0 0 7 cn co r-\\ncm\u00e2\u0080\u0099 cm co\\nco co\u00e2\u0080\u0099 CO\\n^(OlOC0770nO l O OOlT\u00e2\u0080\u0094\\n7 CM CM o co 7 o on CO cm fM o\\nCO 7 7 7 00 to CO 7 7 to 1\\nCo 7 7\\nCM CM\\nCO\\niOLoCMCOT-onCMcn- -co 7 CooocM\\n7 7 CM CM C0^7-7^7CMC00n\\n^\u00e2\u0080\u00a2coi^k 7 co 6 n i- c co\\ncm\\n7tototo7tototo\u00e2\u0080\u0099-~\\nCo 7\\n7C07 l 07000\u00e2\u0080\u0099~-\\nT~ co 7\\n77j l flCMOOOO\\ny- 00 7\\n7tnO)lf)\u00c2\u00bb OOrrCO\\nT- cm T co\\ntotocotototoo-Tto\\ncm y~ 7 co\\nco 7 7\\ncm\u00e2\u0080\u0099 P\\ntoCOtoCMCOtotooO Oto77?-lto\\n7 J in 0 r^ppr-i^-K cooo\\n0 CM rs *OCMC0CO^-^ O)\\nK 7 7 1 1 Y o\\nCMOCOCOOOO 77\\nCM co\\nV)\\n0\\no\\nv\\no\\nv_\\no\\no\\nO)\\n11\\n2 m\\n2 c w\\n.2073\\nO Q. o ~0\\nO Q-\\nw\\ni 10\\nUJ\\no\\nLL\\nQ\\nw\\nI-\\nQ\\n\u00e2\u0096\u00a0o 0 co\\ns#s\\no\\n\u00c2\u00b0a\\nw\\n0\\no\\n!c\\n0\\nU)\\n0\\no\\n3\\nQ\\nx:\\nCD\\nV)\\nu\\ns\\nO)\\n\u00e2\u0096\u00a0c\\n.O)\\nw\\nnc\\no\\n3\\nco\\n0\\no o\\n19\\nE 2\\nO)\\ncm\\nCO co\\no o\\n2 5\\nCO CO\\nco S\\nO) On\\n\u00e2\u0080\u00a2O -o\\nI I\\nO) .On\\nCO\\n0\\no\\nsz\\n0\\nCO\\n0\\nD\\nI-\\n0 .2\\nX Q\\nCO\\n0\\no\\n\u00e2\u0096\u00a0c\\ns\\nUj\\nI\\n2 -c\\n0\\n6\\n0\\n01 S 0\\n0 W\\n0 0\\n-2\\n3 3\\n0 5\\n0 .05 O)\\n1\\nfO 0\\no\\n2 o\\n~n\\nQ 0 S\\nO s\\no cr O\\nrZ. Q)\\nDC c 3\\n\u00e2\u0096\u00a02\\n0\\n0\\n0\\n5\\n0\\n0 0\\nc\\n.0\\n2 ^2\\n5 03\\n0\\n-g\\no -S\\nc\\n0\\n05\\n.0\\n0\\ns\\no\\nc\\n0\\nc\\n0 0\\n\u00e2\u0080\u00a22 c\\n0 s\\n8 e .1\\n.c\\nc\\n0\\n5\\n2 p 7 6) D i _\\no -c co B- 9 o\\ni5 45 ig 1 5 0 2 2\\nAppendix A National Emissions (1970 to 1998) A-9", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0209.jp2"}, "210": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nT5\\n0\\n3\\nC\\nC\\no\\nCM\\n0)\\nn\\n0\\nH\\n00\\n05\\nCO\\nC5\\nC5\\nCM\\n05\\nCO\\n03\\no\\nCO\\nCO\\nCO\\n05\\nT\u00e2\u0080\u0094\\n03\\noo\\nCNJ\\nCNJ\\n05\\nT\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\ncnj\\ni\u00e2\u0080\u0094\\nr^\\nco\\nco\\nco\\nCO\\nCM\\no\\n03\\no\\nCNJ\\n00\\nK\\nO\\n03\\nCO\\nCNJ\\nCNJ\\nCD\\nT_\\ncnj\\nCD\\nCD\\nCO\\nco\\nK\\ncp\\n1\u00e2\u0080\u0094\\nCO\\n03\\nCO\\nK\\nK\\no\\n05\\n03\\nt-p-\\nCNJ_\\nCNl\\nC5\\nY\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094\\nCNj\\nT\u00e2\u0080\u0094\\nLO\\n05\\nco\\nCO\\nN}-\\n05\\nK\\nO)\\nCO\\n05\\nK\\nCO\\n00\\n05\\n03\\nCNJ\\n05\\nY*\u00c2\u00bb\\nT\u00e2\u0080\u0094\\ncnj\\nCO\\nQ\\no-\\n05\\nCO\\n03\\noo\\nK\\nK\\nCO\\nK\\n05\\n03\\nco\\nCNJ\\n05\\nT\\ncnj\\nT\u00e2\u0080\u0094\\nCO\\no\\nCO\\nCO\\nCO\\n05\\nCO\\n03\\nt\\nCO\\nCO\\nCO\\nto\\n05\\n03\\nCO\\nCNJ\\n05\\nymm\\ncnj\\nCM\\nLO\\nCO\\nCO\\nlO\\n\u00e2\u0096\u00a0M-\\nCO\\nK\\n03\\n05\\nCO\\nCO\\nCO\\nCO\\nco\\n03\\nco\\nT\u00e2\u0080\u0094\\nCNJ\\n05\\nT\u00e2\u0080\u0094\\ncnj\\nT\u00e2\u0080\u0094\\nCNJ\\nCO\\no\\nCO\\n05\\nN\\nCM\\n03\\nLO\\nCNl\\nr o\\nCO\\nT--\\nCO\\n03\\nLO\\nT\u00e2\u0080\u0094\\nCNJ\\n05\\nT\\nCNl\\nO\\nCO\\nCO\\nCNJ\\nCO\\nCO\\n00\\nN-\\n03\\nO\\nCO\\n^5-\\n05\\nN\\n03\\nLO\\np\u00e2\u0080\u0094\\nCM\\nCO\\ncnj\\n03\\nCNJ\\nCO\\nCO\\nQ\\nC5\\nK\\nCO\\n00\\nK\\nM-\\nK\\nK\\n03\\nO\\no\\nCM\\nCO\\nT_\\ncnj\\nT\u00e2\u0080\u0094\\nCO\\n05\\nCNl\\nCO\\nCO\\nCO\\n00\\nCO\\nCNl\\nCO\\nK\\nCO\\nCO\\nCO\\n03\\no\\nCM\\n00\\ncnj\\nLO\\nLO\\nCNJ\\nCO\\no-\\nJN\\nCO\\no-\\nCO\\nLO\\no-\\no-\\nCM\\nCC5\\nco\\n03\\n05\\nCM\\nK\\nT_\\nCNl\\no\\nCO\\nCNl\\nCO\\nCO\\n05\\nCO\\no-\\nco\\nCNl\\nS;\\n05\\n03\\noo\\nT\u00e2\u0080\u0094\\n05\\nT\\nCNl\\nLO\\nCO\\nCNl\\n05\\nQ\\nCO\\nCO\\nCO\\nh-\\nCO\\nco\\nCO\\nT\u00e2\u0080\u0094\\nSN\\no-\\n03\\nco\\nCO\\nt-\\nK\\nT\\no\\n05\\nO\\nCO\\nK\\n05\\n05\\nY\u00e2\u0080\u0094\\no\\nCO\\nT\u00e2\u0080\u0094\\nIS\\nCO\\n05\\no-\\nCM\\nCO\\no\\no\\no\\nTO\\nO\\nID\\nO\\n3\\nO\\nCO\\nco\\nc\\\\j CO\\no\\no\\no\\n-rSOlOlOCOTt jTtoO\\n-O CO Y M- Osl CM\\nO) 1- Co CO\\n05 m-\\nCO CO 05 NJ-\\nN.\\nK\\nK\\n05 M- 05\\nV\\n05\\n3\\nc\\nc\\nO\\nLi\\no\\n1\\nQ\\n2\\n0\\n3\\ns\\nQ\\nO\\nQC\\n2\\nO\\n2:\\n\u00e2\u0080\u00a2o\\nCO\\no\\nac\\nc\\no\\n2\\n\u00c2\u00ab0 _\\nS 0\\nc\\no\\no 76\\n3 c\\nc -3\\n5 -8\\nO p-\\no -S\\nc\\nI\\nS\\no\\n\u00e2\u0080\u009cS\\ni\\nCO\\n05 00 O 05 CO\\nK LO\\nCM CO 0- 00 CO\\n05\\nCO K\\nLO\\nCO\\nco\\no\\nK\\no\\nCD\\nm:\\nCM\\nCO\\nCO\\nCD\\nY\u00c2\u00bb\\nCO\\nCO\\no\\no\\nT\u00e2\u0080\u0094\\n\u00e2\u0096\u00a0d-\\nCD\\nk\u00e2\u0080\u0094\\n05\\nco\\nY\u00e2\u0080\u0094\\nLO\\nCO\\nt\\nYY\\no\\nCM\\n05\\n05\\n05\\nY\u00e2\u0080\u0094\\n\u00e2\u0096\u00a0O-\\n\u00e2\u0080\u00a2O\\n00\\no\\n\u00e2\u0080\u00a2o-\\nE\\nCM\\nCD\\no:\\nLO\\nO\\nIP\\no\\nO\\nT\\nCM\\nl\\nCO\\n05\\nCO\\nCO\\n00\\no\\no\\nT\u00e2\u0080\u0094\\nCO\\nCO\\nN.\\nY\u00e2\u0080\u0094\\nCM\\nr-~\\nco\\nCO\\nto\\n\u00e2\u0096\u00a0St\\nc\\n05\\n05\\n05\\nY^\\n5-\\n\u00e2\u0096\u00a0O\\nCO\\n*o\\n\u00e2\u0080\u00a2rf\\n0\\nCM\\n_c\\n\u00e2\u0080\u00990\\nCO\\nCD\\nCO\\nJQ\\nCD\\nCO\\nO\\nY\u00e2\u0080\u0094\\n05\\nK\\nm\\nO\\no\\nr\u00e2\u0080\u0094\\nY-\\nc\\nCO\\no\\nY-\\no\\n05\\nCO\\nCO\\nCO\\n2\\nco\\nCM\\no\\n05\\nCO\\nY\u00e2\u0080\u0094\\nCM\\n05\\nCM\\nCM\\n05\\no\\n0\\nCM\\nk_\\n0\\n05\\nO\\no-\\n05\\nY-\\nCy\\nLO\\nCO\\n05\\nCD\\noo\\no\\no\\ny\u00e2\u0080\u0094\\nCM\\n3\\nCM\\nCD\\nY\u00e2\u0080\u0094\\n05\\nfr\\nco\\nCM\\nCO\\n05\\n2\\nco\\nr^\\nJD\\n05\\nCO\\nY-y\\nCM\\n05\\nT-\\nY^\\nCO\\nCO\\nco\\n0\\nin\\nCM\\n0\\ni-y\\nO\\nCO\\n05\\nY-.\\nLO\\n05\\nCD\\nY\u00e2\u0080\u0094\\no\\no\\nT _\\nO\\n_0\\n05\\nY-^\\nO\\n\u00e2\u0096\u00a04t\\nto\\nCM\\nCO\\n2\\n2\\nco\\n05\\nto\\nY\u00e2\u0080\u0094\\nCM\\n05\\nY\u00e2\u0080\u0094-\\nCM\\nCM\\n05\\n*0\\n\u00e2\u0080\u00a2O\\n0\\nCM\\nTD\\n0\\nY\u00e2\u0080\u0094\\nCD\\ni\u00e2\u0080\u0094\\nco\\n05\\no-\\nCO\\nCO\\nIC5\\n05\\n1\u00c2\u00b0\\nCO\\no\\no\\nT\u00e2\u0080\u0094\\nCD\\nO\\nCO\\nPJ\\nY^\\nY\u00e2\u0080\u0094\\nfr\\nin\\nY\u00e2\u0080\u0094\\nCO\\nto\\n2\\nin\\n05\\nE\\n05\\nCO\\nY~\u00c2\u00ab-\\nCM\\n05\\nY\u00e2\u0080\u0094\\nCM\\nCM\\nin\\nYf\\n0\\nCM\\nH\\n\u00e2\u0080\u00a24-\u00c2\u00bb\\nLO\\nCD\\n05\\nCO\\nCD\\n05\\nC5\\n00\\nCO\\nin\\n05\\n0\\n05\\n05\\no-\\nCO\\nY\u00e2\u0080\u0094\\nY~y\\nCM\\nCM\\nCM\\n05\\nCD\\nY\u00e2\u0080\u0094\\nco\\nOo\\nCM\\n2\\nS\\nco\\nCM\\n2\\n2\\nrr\\nCM\\n0\\n_Q\\n\u00e2\u0080\u00a2O\\n0\\nCM\\n0\\nCO\\nCD\\nCD\\nCD\\n05\\n05\\nY-\\nCO\\nCo\\n05\\nco\\nT\u00e2\u0080\u0094\\n05\\n0\\n05\\nCO\\nCO\\nY\u00e2\u0080\u0094\\nY-\\nY\u00e2\u0080\u0094\\n05\\nCM\\n05\\nt\\nCD\\nY\u00e2\u0080\u0094\\nco\\nCO\\nCO\\n2\\n2\\nCO\\nCO\\n2\\n2\\n\u00e2\u0080\u00a2O\\no\\no\\nc\\n\u00e2\u0080\u00a2O\u00e2\u0080\u0099\\nCM\\nQ)\\nk_\\n0\\nr^-\\nO\\nCO\\n00\\n\u00e2\u0096\u00a0q;\\nCO\\nm\\nCO\\nco\\nCO\\nCO\\nCO\\nLO\\nr-\\nCM\\nco\\nY\u00e2\u0080\u0094\\nY*\u00c2\u00bb\\nCM\\n05\\nco\\nY\u00e2\u0080\u009c\\n05\\nCO\\n05\\nCM\\n2\\n2\\n05\\nCM\\n2\\n2\\nz\\n05\\nco\\n00\\n03\\ntJ- t\u00e2\u0080\u0094 O O\\nCO O 05\\ny- fY LC5\\nfY 05 cm oo\\n05 CM 05 00\\nco y-\\nK\\nR!\\nWCOC\\\\|COO)NOO)K-t\\ny- y~ T\u00e2\u0080\u0094 LO CO Co p,\\nT- LO\\nC50 CNJ CO\\n^Or-KCO\\nCO t- CO\\no 2 o\\nS 2 2 2\\nS CNJ\\n05\\nCNJ\\n3 5\\niy o\\nCO\\nIt\\n|y o\\no\\nCNJ\\no r\\nK 11\\n\u00c2\u00b0SS2\\nCO\\nK co\\nII\\no o 3 S JO s\\nCO Co\\nLO L.\\nco CNJ\\nCNJ\\nr~\\nCD Mt CO\\nSt CNJ\\nII\\n\u00c2\u00b0I\\nI 52\\nco\\n5 o\\n2 2 CO 2 2 2\\n-23\\n05\\nCO\\nCO\\ng\\n05\\nO 05\\nc .c\\n2 c\\nc to\\n05\\ncE \u00e2\u0080\u0099is s\\n_ w -2\\nC 5 t to 03\\n8 g-i\\n2 TO\\n2\\n.co\\n8\\n05\\nE\\nE\\no\\no\\n05\\n.o\\nJO\\n05\\nCO\\nC13\\ntO 05\\nCO c\\nCD\\ns:\\n1111 11\\nCO\\n55-\\n05\\nE\\n3\\n05\\n1\\n05\\nQ.\\nTD\\n.05\\n3\\nCr\\nCO\\n55-\\nOs\\n8\\n3\\no\\n111 CD\\nco O\\nto Uj\\n8 I\\n9-^\\nE -j\\nO -J\\no uj\\no\\n?o\\no\\no\\n/3\\n\u00e2\u0080\u009cO\\nc\\n0\\nCD\\nk_\\n=3\\n3\\no\\nL.\\no\\nCO\\n5 =3\\nn\\nI E\\n3 o\\n\u00e2\u0096\u00a0go\\no 2\\nCO\\nCD\\no\\ns\\nCD\\nco\\n05 Q5\\nc\\nCO O \u00e2\u0080\u0099o)\\nCD O TO\\nI O IL\\nCO\\n05\\nsz\\n4\u00e2\u0080\u0094\\n5\\nO)\\nc\\n\u00e2\u0080\u0098c\\nc\\n03\\n0\\n_Q\\nk_\\no\\no\\n4\u00e2\u0080\u0094\u00e2\u0080\u0099\\nk_\\no\\nk_\\nQ.\\nV\u00e2\u0080\u0094\\na\\n0\\n0\\nc\\no\\nJ)\\nCO\\nE\\n0\\ncn\\n0\\n\u00e2\u0080\u0098k.\\no\\nCD\\n0\\n4\u00e2\u0080\u0094*\\n0\\no\\n0\\no\\nk.\\n3\\no\\n0\\n0\\nk_\\n0\\n0\\n0\\nk_\\no\\nLL\\n0\\nn c\\n0 .b\\n0 0\\n0\\n0 0\\n0\\no\\n0\\nk_\\n03:\\nS 5\\n03\\n0\\nCsJ\\nhY\\n0\\no\\nO\\n03\\n0\\nO\\no\\nk_\\n5\\n3\\n_Q\\nO\\n0\\n0\\n0\\nO\\n_3\\n\u00e2\u0080\u00985\\n0\\n0\\nQ_\\n0\\n0\\nO\\n\u00e2\u0080\u00a24\u00e2\u0080\u0094\\no\\n_Q\\nTO\\n0\\nCD\\n0\\n4\u00e2\u0080\u0094*\\nsz\\n0\\n4\u00e2\u0080\u00944\\no\\no\\n5\\nQ_\\n0\\n4\u00e2\u0080\u0094\\n3\\n0\\nE\\n0\\nk_\\n3\\nO\\nO\\n0\\nC\\no\\n0\\no\\n0\\n_Q\\n0\\n4\u00e2\u0080\u0094\u00c2\u00bb\\nO\\nE\\nc\\nTD\\nTO\\nC\\n3 co\\n0\\no a\\n0\\no\\nY- C/5\\nCO c\\n3\\nO\\n-C\\n4\u00e2\u0080\u00944\\n-C o\\n0\\n0 t\\nBE\\nE\\n0\\nk_\\nCO CO\\n05\\n.2 O\\nE\\nCO\\n05\\nTo in\\n05\\nr- C\\nO\\nTO\\nCO si\\n0\\nt\\nr~\\nC\\n8\\n^,\u00e2\u0096\u00a02\\no\\n*0\\n0\\nc c\\nE\\nE CD\\n0\\nco 23 t\\nQ) 2 CD\\nQ.\\nCD c\\no\\nco o\\no\\n05\\nCD\\no\\nc\\n2\\no\\nc CC3\\nJO\\n05\\n4 1\\no\\nA-10 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0210.jp2"}, "211": {"fulltext": "Table A- 3 Volatile Organic Compound Emissions\\n(thousand short tons)\\nNational Air Pollutant Emission Trends, 1900-1998\\nS CT)(*)COr-^cDcOffi(DT- 0\\no) cm \u00e2\u0080\u0099\u00e2\u0080\u0094co ij n (o co\\nL_\\no\\ns\\nCD\\no\\n0)\\no\\nk-\\n3\\no\\nw\\nIopj in0 DCD 2S9? T n CMO)p^35\u00e2\u0080\u0099}iPNOCM\u00e2\u0080\u0099 lOCMK !t\u00e2\u0080\u0099 !tCMnioCMCOCM\\nCO\\nM n CD K\\nCO\\nOjcOCOOOOlOCOCOCDOCM*--\\nq CVJ t- co tj (o c\\\\|\\nr- Cq\\n^oocmocococmooidC\u00e2\u0080\u0099J\\nq cm i-o r- n cn cd cm\\nc\\\\j oo\\n^ffl jwo^cocMno tco\\nct cm t- o r- co in co\\nfs\\n2\u00c2\u00ae }CMOg0CMT-i-(DCM\\nq cm r- co f\u00e2\u0080\u0094 miococo\\nIs.\\njN\u00e2\u0080\u0099tCMOt\u00e2\u0080\u0099NCMCMOCOCt\\nq CM i-\u00c2\u00ab0 1\u00e2\u0080\u0094 ID \u00e2\u0080\u0099f CO CO\\nT~ 00\\n3 |s.inc\\\\iocpcO\u00e2\u0080\u0099-0\u00e2\u0080\u0099-coio\\nct CM -05 \u00e2\u0080\u0099-COlOCOCO\\noo\\nbNCDCMCMCMNCMCO\u00e2\u0080\u0099-\u00e2\u0080\u0099t O\\nt cm r- in to m N\\nCM fO CO oo CO 03 CO\\nCO CO co\\nnnco\u00e2\u0080\u0099i K\u00c2\u00ae(oOinoc\\\\i\\nT- CM M) o o (O 01 o\\nCO CO CO i\u00e2\u0080\u0094\\nnncooiM-cDcjONConocM\\nt- in ?o co co co \u00c2\u00aeo co\\n|s CO Co T-\\nco M\\nMl CM CO M-\\nCO CM\\nCO co q\\nCO M\\nCM\\nCO CM CO CO CM co Cm\\nq CM T\\ncm cm n co cm co t\\nq CM\\nlO JO q Cf3\\n|s K CO CM\\nco co q 03 t-\\n(O to C CO CM\\nC0\u00e2\u0080\u0099-0)C000\u00e2\u0080\u0099T\u00e2\u0080\u0099TO\u00e2\u0080\u0099 lO\\nCO Co Is CM\\nCOOCOCMCM\u00e2\u0080\u0099T T0 1 Ot-\\nt- CMCM \u00e2\u0080\u0099t\u00e2\u0080\u0099 r-\\nCO CO K CM\\nCMKococococMp fncMCMioir)\\n\u00e2\u0080\u0099-\u00e2\u0080\u0099-COCO IS CO CM CO\\nCM\\nM-\u00e2\u0080\u0099-Ol M-COOOCMpiOCMI -CMCOlO\\ncm co co K co in v\\nCM\\nfCDOCOCMOOCMpCOCMOCMCOlO\\nT- T- co Co Is co CO q\\nCM\\nMNOPO05C\\\\|0)Nnn0|lf)lt)\\n\u00e2\u0080\u0099-\u00e2\u0080\u0099-COCO COCO 00 q\\nCM\\nncDCO(Op\u00e2\u0080\u0099r\u00e2\u0080\u0099TO)OcO\u00e2\u0080\u0099 M CO* COOO)CMKCOnoOC\\\\|M-lO\\nI s 2 2 CO O rv.\\nis. is\\nK CM\\nCM co co\\nCO CO CO q\\nCM\\nC0C0C0C0C0 r TC0CtCMOrfO0)C0C0C0CM\u00e2\u0080\u0099 0)CMCMCMI3)^\\n\u00e2\u0080\u0099-r~ cocoo) cm co cm cocm q co\\nvo t\u00e2\u0080\u0094\\n(M\\nfs IS. |S. CM\\nCO CM\\nrs fs CM\\nco CM\\nCO\\nCO\\nco CM\\no- CO\\nq CM\\nCO\\nin\\nin\\nm\\nCO\\nr-\\nco\\nin\\n0\\nIS\\nst\\n03\\n03\\n\u00e2\u0080\u00a2q;\\nq\\nin\\n03\\nfs\\nCM\\nO\\nfs\\nCO\\nin\\n03\\nK\\nTs-\\nCO\\nC3\\nCO\\n03\\nCO\\nIS\\nK\\nT\\nco\\nCO\\n1\\nc\\nCO\\nCO\\n\u00c2\u00ab0\\n00\\nCM\\nCO\\nq\\nq\\n03\\nCO\\n00\\nin\\nN\\nT\u00e2\u0080\u0094\\n03\\nCO\\nT-\\nco\\nT\\nCD\\nCO\\nLO\\neo\\nCD\\n\u00e2\u0080\u0099O\\nin\\nin\\nq;\\nq\\nfs\\nSi!\\nfs\\nCM\\nO\\nCO\\n0\\nCO\\n03\\nfs\\nq\\nq\u00e2\u0080\u0094\\nCO\\nCM\\nCO\\nco\\nK\\nT-\\ns\\nCO\\nT\\neo\\nin\\nin\\n5\\nco\\nco\\nCM\\nco\\nq\\nq\\n03\\nco\\n03\\nin\\ni\u00e2\u0080\u0094\\n03\\nCO\\nCO\\nT_\\nr-\\nr-\\nm\\nco\\nS3\\nTf\\nCO\\n\u00e2\u0080\u0099t\\nCM\\nq:\\nq\\nco\\n03\\nCM\\nCO\\nq\\nSP\\nK\\nco\\nfs\\nO\\n03\\nfs\\nCO\\nCO\\nCM\\nT\u00e2\u0080\u0094\\nCO\\nm\\nco\\n0\\n|s\\nK\\nCO\\nq\\nCM\\nCM\\nCO\\nq\\nfs\\nCM\\nq\\nin\\nC0_\\nCO\\nCO\\nco\\nco\\n,_\\nT\u00e2\u0080\u0094\\nco\\nCM\\n03\\nco\\nCO\\nfs\\n03\\n03\\nq;\\nq\\n00\\nn\\nq\\nO\\nq\\nO\\nr^\\n0\\nco\\nq\\nq\\nCO\\nq\\nT\u00e2\u0080\u0094\\nSN\\nin\\nCO\\nCO\\nZ\\ns\\nz\\nO\\n00\\nO\\nC30\\nz\\nZ\\nCM\\np3\\nin\\nco\\n00\\nz\\nCO\\nq\\nZ\\nz\\nCM\\n03\\nCM\\n03\\nco\\nCO\\nCM\\nT~~\\nin\\n0\\nCO\\nis\\nO\\n0\\nq\\nq\\nCO\\n03\\nq\\nCO\\nP3\\n03\\nco\\nq\\nq\\nSQ\\nK\\nco\\n03\\n03\\nco\\nr-\\nf7\\nis\\nz\\nlx\\nz\\nCM\\n\u00e2\u0080\u0099t\\nCM\\nM-\\nZ\\nZ\\nCO\\nto\\nCO\\n1\u00e2\u0080\u0094\\nin\\nIS\\nZ\\nq\\nfs\\nCM\\n03\\nZ\\nZ\\nS?\\nCM\\nCM\\n(s\\n03\\nCM\\nIS.\\nin\\nCO\\nO\\nO\\nq\\nq\\n0\\n03\\n00\\nq\\n03\\nP\\nco\\nq\\nq\\nq\\n03\\nin\\nO\\nIs\\nO\\nis\\nCO\\nz\\nIn\\nz\\nco\\n\u00e2\u0080\u0099t\\nCO\\nM-\\nZ\\nZ\\n|s\\nq\\nCO\\nCM\\nCO\\nZ\\nCM\\nfs\\nq\\n00\\nZ\\nZ\\n03\\n03\\nco\\nCM\\np\\nGi\\nUJ\\n-J\\nUJ\\nod\\n5\\no\\no\\n\u00e2\u0096\u00a0*4\\nUJ\\nw\\nCD\\nO CD\\nc\\no\\nCO\\no\\nJO\\nE\\no\\no\\nId\\nc\\nk_\\nCD\\n3\\ncn\\nQ\\ni\\no\\no\\n\u00e2\u0096\u00a0i 5\\nCD\\no CD\\no o o\\nCD CD CD\\nC C f\\no o\\nD\\nc\\no\\nGO\\nc\\nUJ\\nu.\\nUJ\\ns E l\\nf o I\\no Q\\no See e\\n^000\\n50 E E E\\n\u00c2\u00ab\u00c2\u00ae55\u00c2\u00b0EEE\\no=ffl\u00c2\u00a3Ssio nn\\nO O CD O Uj O\\nca g\\n\u00e2\u0080\u0098o o\\nU O\\no o\\n.g\\nc\\nco\\n\u00e2\u0080\u00a2g\\nc/3\\nCO\\nGC\\nQ.\\nCO\\no\\nX\\nw\\n4 o\\no Z\\n1\\nLL\\nsiS\\nMl 0\\n2 cc\\nI\\nh-\\no\\nQ\\no\\nDC\\n0.\\nQ\\nUJ\\nC/3\\no\\n1\\no\\n1\\nCO\\n.c\\no\\n.g\\nc\\nCO\\n\u00e2\u0080\u00a2g\\nw\\nCO\\nOC UJ\\n3\\n-I\\n2\\no 53\\n2 E\\nCD -C3\\ng !5\\nE o S\\n0 E\\no o\\n53\\nE\\nTO\\no\\nCD\\n.0\\nca\\n\u00e2\u0096\u00a0c\\nS\\nE E\\nCO\\n5\\no\\nE -c l\\na o\\ns_\\no\\no\\nCD\\n03\\ns\\n0\\n0\\n0\\nCO\\nco\\n0\\nI\\na\\nc:\\n.0\\n1\\n03\\nr\u00c2\u00a7\\n0\\nE\\n0\\n.co\\n\u00e2\u0080\u00a2s\\n1\\n8\\n0\\n0\\nI\\nI\\nE\\no\\no\\nCO\\n03\\n-c\\no t;\\no\\nc\\nCD\\ng\\nE\\n03\\n-C\\no\\ng\\nc\\nCD\\no\\n03\\nE\\nc\\nco\\nCD\\nCE\\ns. i_\\n2 S\\n03\\nE\\n2s\\no\\nCL\\nE\\n03\\nt\\ni\u00e2\u0080\u0099\\no\\na\\nCO\\n.c\\nCO\\n2\\n03\\nc\\nI\\no\\na\\nAppendix A National Emissions (1970 to 1998) A-ll", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0211.jp2"}, "212": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n~o\\nQ)\\n3\\nC\\nQJ\\nn\\n0\\n00\\nK\\nCO\\n00\\nCO\\nco\\nCM\\n00\\nCO\\n00\\nr*.\\nCO\\n3\\n\u00e2\u0096\u00a0M-\\nIP\\n00\\nCD\\nP\\nP\\nK\\nO\\np\\noo\\nY\\nco\\nK\\nP\\np\\nP\\np\\nCD\\n00\\nT\u00e2\u0080\u0094\u00e2\u0096\u00a0\\no\\nCM\\nk\\nCO\\nN,\\nco\\nCD\\nco\\nCM\\nTk\\np\\nP\\nO)\\nT\u00e2\u0080\u0094\\nY\\nCM\\nCM\\nTk\\n3\\nK\\nCO\\n00\\nco\\nco\\nCM\\noo\\nm\\n00\\nY\u00e2\u0080\u0094\\nCO\\nCD\\nM-\\n5P\\n00\\nN\\nP\\nK\\nO\\nD\\nO\\nY\\nco\\nK\\nP\\np\\nP\\np\\nO)\\nCo\\nk\\no\\nCM\\nTk\\nco\\n1\\nP\\nCD\\nCM\\nTk\\nCD\\nCD\\nCD\\nY\\nCM\\nCM\\nTk\\nCO\\nkk\\nlo\\n00\\nDk\\nco\\nCM\\n00\\nco\\nSk\\nY\u00e2\u0080\u0094\\nCO\\nCD\\nCO\\nCM\\n00\\n\u00e2\u0080\u00a2\u00e2\u0096\u00a0tf\\nY\\nP\\nIP\\no\\nCO\\nCk\\nCD\\nCM\\np\\nP\\n\u00c2\u00a32\\np\\nCT\\nK\\nk\\nt-k-\\no\\nCM\\nTk\\nCO\\nK\\nP\\nco\\nCD\\nT-\\nTk\\nCD\\no\\no\\nY\\nDl\\nCM\\nT\u00e2\u0080\u0094\\nco\\nCNj\\nCO\\nCM\\nin\\n00\\nco\\nCM\\nCO\\nrf\\nCM\\no\\nY-k\\nK\\nP\\np\\nP\\nCD\\nTk\\n00\\nCM\\nP\\nP\\np\\np\\nP\\nTk\\nSt\\nY\\nCT)\\nk\\nCM\\nk\\n00\\nCO\\nCM\\nCO\\nP\\nCM\\nCM\\nCD\\nCM\\nP\\n3\\nP\\nCO\\nTk\\nY-t\\nTk\\np\\nCD\\nT-\\nT**\\nT\u00e2\u0080\u0094\\nTk\\nk.\\nP\\nCO\\nTk\\nCt\\nCO\\nCO\\nCO\\nco\\nD-\\nCO\\nk\\nCO\\nCM\\nK\\n\u00e2\u0096\u00a0Yk\\nK\\nP\\nO\\nr-.\\nP\\nCD\\n00\\nN\\nP\\nP\\nN\\np\\no\\nCD\\nCO\\nCO\\nCD\\nk.\\nM-\\nk\\nCM\\nCO\\nCM\\nCM\\nTk\\nCM\\nCM\\nCD\\nCM\\nP\\nY\\nO\\nCO\\nTk\\nY\u00e2\u0080\u0094\\nO\\np\\nO)\\nT\u00e2\u0080\u0094\\nk\\nTk\\nT~\\nP\\nP\\nCO\\nTk\\nTk\\nCO\\nK\\nN\\nCM\\nDk\\nCO\\nCO\\nk\\nCO\\nCD\\nCO\\nY-k\\nCD\\n^k\\nK\\n\u00e2\u0096\u00a0o-\\nCO\\n00\\nK\\nCD\\nCM\\n00\\nCD\\nO\\nCD\\nn.\\np\\nY-.\\nCD\\nSt\\nCO\\nCJ\\nCO\\nk\\nM-\\nk\u00c2\u00bb\\nCM\\nCD\\nk\\nCM\\nCM\\nCM\\nCD\\nCM\\nP\\nY\\nCO\\nTk\\nY\u00e2\u0080\u0094\\nCD\\np\\no\\nk\\nT.\\nk-\\nP\\nCO\\nCO\\nTk\\nTk\\nCM\\nco\\nCO\\nCM\\nco\\nCO\\nk\\n\u00e2\u0096\u00a0Tf\\nCD\\nCO\\nY-k\\nk-\\n^*k\\nP\\ns-\\nfk\\no\\nK\\nCD\\nP\\nCO\\nCM\\nCM\\nK\\np\\nY-k\\nCO\\nCO\\nCD\\nK\\nk\u00e2\u0080\u0094\\nM-\\nk\\nCM\\nCD\\nk\\nCM\\nCM\\nCM\\nT\u00e2\u0080\u0094\\no\\nCM\\nP\\nCO\\np\\nCO\\nT\u00e2\u0080\u0094\\nY-k\\nCD\\np\\nCD\\nk\\nk-\\nTk\\nP\\nCM\\nCO\\nTk\\nTk\\nT*\\nk\u00e2\u0080\u0094\\nLTJ\\nr-k\\nCO\\nin\\nk\\nCD\\nK\\nTk\\nCO\\nYk.\\nP\\ncp\\nCD\\nCD\\n\u00c2\u00a3N\\nCD\\nP\\nCD\\nP\\n(k\\nK\\nK\\nY\u00e2\u0080\u0094\\nP\\np\\nCO\\nCD\\nCO\\nk\\nM-\\nT-\\nk\\nCM\\nrk\\nk\\nCM\\nP\\nCM\\nCD\\nCM\\nP\\nY\\nO\\nCO\\nT\u00e2\u0080\u0094\\nYk\\nCD\\np\\nCD\\nk\\nTk\\nT\u00c2\u00bb\\nP\\nCO\\nCO\\nTk\\nO\\nin\\nK\\nCO\\nTj-\\nCO\\nk\u00c2\u00bb\\no\\n00\\nCD\\nY-k\\n\u00c2\u00a37\\n3\\nIP\\nCM\\nCO\\nOO\\nP\\nK.\\nYk\\nr-k\\nP\\n00\\nN.\\nP\\nYk\\n2?\\nK\\nCO\\nO)\\nk\\nCO\\nk\\nCM\\nin\\nCM\\nCM\\nCM\\nCD\\nTk\\nhs\\nTk\\nO\\no\\nT.\\nY-k\\nCD\\nN\\nCD\\n1\\nT\\nT.\\nT\u00c2\u00ab\\nP\\nCO\\nCO\\nTk\\nCD\\nC3\\no\\nCO\\nCM\\nCO\\n00\\nCO\\n00\\nCM\\nCO\\nCO\\nCM\\nin\\nN\\nP-\\nCD\\nCM\\nCO\\n25\\nP\\nCO\\n00\\np\\nTk\\nCO\\np\\np\\nCO\\n00\\nlO\\nco\\nt\\nCO\\nCM\\nTk\\nP\\nhk\\nP\\nT.\\np\\nr 5\\nCD\\nCD\\nTk\\nco\\nY\u00e2\u0080\u0094\\np\\nY\\nCD\\nC\\\\J\\np\\np\\nY\\nCO\\nO\\no\\nCM\\nco\\n00\\nCD\\nCO\\nCM\\nCO\\nCO\\nCO\\nin\\nco\\nCD\\nCM\\nCO\\nCD\\np\\nCO\\n\u00c2\u00a32\\nCO\\np\\nK\\nCO\\nco\\nlo\\nT~k\\n\u00e2\u0096\u00a0O\\nco\\nCM\\nY--\\n00\\nN\\nP\\nY\u00e2\u0080\u0094\\nP\\nY\\nfk\\nik\\nTk\\nco\\nY-k\\np\\nY\\nCD\\nv\u00e2\u0080\u0094\\nOq\\np\\np\\nY\\nm\\nK\\nin\\nCM\\noo\\n00\\nCD\\nCO\\nin\\nSP\\nCM\\nCM\\nM\\nTk\\niP\\nOO\\nCM\\nCO\\nY-k\\n\u00c2\u00a33\\nrk\\nCM\\np\\nS\\nlo\\np\\nY\\nCO\\n00\\n\u00e2\u0096\u00a0M-\\nk~\\ni\\nCM\\nCM\\nYk\\n00\\nK\\ni\\np\\nY-k\\np\\no\\np\\nT\u00e2\u0080\u0094\\nco\\nYk\\nK\\nP\\nCD\\nC\\\\l\\nT\u00e2\u0080\u0094\\nn\\np\\nY\\no\\nCD\\nP\\nK\\nm\\nco\\n\u00e2\u0096\u00a0q;\\nDk\\nCM\\ncvi\\nCO\\nY-k\\np\\np\\np\\nPJ\\nTk\\nY\\n2!\\nCD\\n00\\nCD\\nD\\nk\\nK\\nN\\nz\\nco\\nCO\\nN\\nCD\\nCD\\nz\\nz\\nz\\nz\\nK\\nCM\\nZ\\nr~\\nCM\\np\\nTk\\nz\\nOvJ\\nYk.\\nZ\\nY\\nY^\\nrk\\nco\\nY\\nCD\\nCO\\nCM\\nz\\nZ\\nP\\nP\\nT_\\nT-\\nk\\nm\\nCD\\npo\\nM-\\nco\\nCO\\nin\\nCM\\nP\\nCD\\nN\\nO)\\nP\\nco\\nTk\\nK\\ny:\\nY\\nCO\\n00\\nCD\\nM-\\nk\\nCO\\nlO\\nz\\nco\\nCO\\nm\\nO\\nCD\\nTkk\\nz\\nz\\nz\\nz\\nco\\nz\\nCO\\nCO\\n00\\nTk\\nz\\nY-.\\nz\\nP\\nco\\nP\\nP\\nCO\\nP\\nz\\nZ\\np\\np\\nT~\\ny\u00e2\u0080\u0094\\nTk\\nO\\nCM\\nK\\nk\\no\\nin\\nIP\\n\u00e2\u0080\u00a2*t\\nP\\nN\\nY\\nCO\\nY\\nK\\nY\\nY\\nY-.\\nr^-\\nCD\\nk\\nN.\\nCO\\nz\\n5\\nCO\\nz\\nt\\nr-k\\nCM\\nK\\nCM\\nz\\nz\\nz\\nZ\\np\\np\\nz\\nCD\\nCO\\nTk\\nCM\\nZ\\nK\\nYk\\nz\\nP\\nTk\\nY\\nrk\\ntk\\np\\nP\\nz\\nZ\\nR!\\n1\\no\\nm\\n0\\n4-\u00c2\u00ab\\nu\\no\\nV\\no\\nk.\\n3\\no\\nC/5\\nV\\n0\\n3\\nC\\n45\\nC\\no\\nI\\nK\\nO\\nQ\\nO\\nOC\\nCX\\n-J\\n-I\\n-J\\n3\\n1\\nO\\n\u00e2\u0096\u00a0o\\n0\\n3\\nC\\nc\\no\\nO\\nO)\\nI\\n0\\nCO ;Q\\n0\\ntE .o\\n\u00c2\u00b0S qi\\nI\\nJ S to\\no\\nCL\\nv.\\n0\\n-Q\\n-Q\\n2\\nCD\\nc\\n.0\\n\u00e2\u0096\u00a06\\n3\\nCD\\n0\\ne\\ncc\\nC\\no uj\\n*5 i-\\n_ CD CD\\nco 2. c\\n\u00e2\u0080\u00a29\\nco -c\\nr: _|\\nCD CD jD\\nis E\\n\u00e2\u0080\u00a2a i\\nCD\\nC\\n2\\nto O\\ni\\nj=\\n3 .0 _ c.\\n\u00c2\u00a30 C 15\\ng 5\\nC Q. O\\nCD 0\\nCL\\n0\\no\\ne\\n0\\ndz\\nO\\nE\\nro x:\\nd sc\\ncl O\\n4e\\no\\n0\\n-Q\\nC\\no\\n\u00e2\u0096\u00a0e\\nco\\no\\nCO\\na\\n5\\nO 1)\\nCD O\\nte co\\nw E\\nCD 0 3\\n-2\\nSo-*\\n.v C Jj\\nc 3 S\\nr. co -q\\n2 2 c\\no k.\\n\u00e2\u0096\u00a0s a\\nc 5* co\\nQ. 2 O o\\nCD\\nc\\nM\\nCO\\n0\\no\\no\\nCO\\n.0\\no) 12\\ng cd z\\nco\\nc\\nCO\\na\\nej\\n2\\n0\\nif) S3\\n|L (D\\nO\\nO CO\\nGC\\ni S\\nif) 0\\n3 O\\nK ~z_\\n0 rv\\n0 2\\n0\\no ys\\no\\nL_\\nCL\\nto O\\nc\\nI2\\nS o\\n0 CD\\n3\\nO O\\nt\\n0\\nLL\\nO\\n\u00e2\u0080\u00a28\\n2\\n9-\\nc\\no\\na 0\\n4C r-\\no\\no o\\no\\nLU\\nz\\nCD\\nUJ\\nQ\\nZ\\nQ\\n\u00e2\u0080\u00a2J\\nUi\\nQC\\n0\\n0\\n\u00e2\u0080\u0098k.\\nco\\n3\\nXJ\\nC\\nD\\n0\\n75\\n0\\ncc\\n\u00c2\u00b0a\\n0\\n0\\n2 E iS\\n0\\n0 \u00c2\u00aba\\n8\\ns o \u00c2\u00b03\\nTT rsl\\n0\\no 0\\n3 c\\nO *0\\nDC\\n0 E\\n0 3\\nO 0\\no\\n\u00e2\u0080\u0098\u00e2\u0096\u00a0C co\\nC\\n3\\n2\\n0\\n2\\n3\\nco\\n\u00e2\u0096\u00a03\\n3\\n3\\nO\\no\\nc\\n3\\nCD\\n0\\nO CL\\n0\\n0\\n0\\nCL\\nco\\n\u00e2\u0080\u00a2\u00e2\u0099\u00a6i\\n1\\n.C\\n2\\nE\\n3\\n0\\n20\\n0\\nQ. O\\n0\\nCD\\nC\\no\\n0\\nc\\n03\\nA-12 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0212.jp2"}, "213": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n~o\\nD\\n3\\nC\\nMB\\nc\\no\\nCO\\nI\\nQ)\\nA\\n0\\nd\\no\\nol\\n4)\\n4-\u00c2\u00ab\\nro\\no\\na\\no\\nw\\n3\\no\\nCO\\np m P P\\nlf M r~ t-\\nT-\\nn Tt lO (O\\n3 oj\\nq i\u00e2\u0080\u0094\\nP O P CO\\nCNj r\\\\i yy yy\\nT-\\nO N 0 lo\\nlo -^3- C\\\\|\\nq i\u00e2\u0080\u0094\\nto W (O t\\nP q r CM\\nq 1\u00e2\u0080\u0094\\nCM CO P q\\n3 c\\\\i\\nO\u00e2\u0080\u0099 i\u00e2\u0080\u0094\\nq |y. 03 CM\\ny- CM y- yy\\nq y\u00e2\u0080\u0094\\ny- O P P\\np ro T\\nCO T-\\nCO CO M\\nO CO CM\\nM 1 y\u00e2\u0080\u0094\\nP p P P\\nO N f c\\\\|\\nO- T-\\nP o q\\nQ N U) C\\\\|\\nn Y~\\nw\\no\\no\\nTO\\no\\n\u00e2\u0096\u00a0O\\n0\\nTO\\nc\\nCM CM\\nq CO\\nCM yy\\nq CO\\nO P\\nq p\\nIX C3\\nq CO\\nCO 00\\nq CO\\nCO Co\\nq CO\\nq\\nq CO\\nq CM\\nq CO\\nCO Co\\nq CO\\nf- CM\\nP co\\nCM P\\nCO co\\nm\\ncm co\\nco\\nCM CO\\nq\\ncn co\\ni- M- CD\\nCM P\\nCO T-\\nco\\no\\nq\\n03\\n03\\n03 CM\\n03\\nCO\\nO\\nCM\\n03 CO\\nq\\nO CO\\nCO\\nT- CO\\nCO\\nCM CO\\nCO\\nq co\\nCO\\n03 in\\nCO\\nco co\\nm\\ncm\\nq CO\\nco\\ncn CO\\nO O) CO\\n03 CO q P\\nCO 1-\\nIx T- yy q\\nCO 03 CO CO\\nCM i-\\n\u00e2\u0080\u00a2n cm r-\\nCO CO CO K\\nCM T-\\np 00 03 in\\nfx O P O\\nCM CM r\\nt- 03\\nin q\\nco \u00e2\u0096\u00a0q;\\no- q;\\nZ\\ncn q;\\nq\\nq\\n-q\\nq\\nCM\\nq\\nZ\\nz\\no3\\nTO\\no\\nU- _0\\ns\\n2 0\\n\u00e2\u0096\u00a05\\nO 53\\nk.\\nCD\\nCD\\nc\\n03\\nCt3\\nc\\n0\\nco\\ng\\n0\\n57\\nto a\\n-Q\\nC/3\\no\\n5\\nD\\no\\n0\\nk_\\n03\\nQ.\\nCL\\noS\\nk-T\\nCD\\n0\\n0 cn\\n-C 0\\n0 s\\n,0\\nCO CM\\ncn\\nCO CO\\nin\\nco n\\nin\\nq 0\\nin\\nco o\\nin\\nco\\nCM\\nCM t-\\nco\\nq\\nco\\nq\\nY- O\\nq\\nq q\\nq q\\nm in\\no co\\nco co\\nco 03\\nCM\\nco 03\\nCM\\nin 0\\ncm\\nq; q;\\nz z\\nII\\ncn\\n0\\nX3 O\\nO =3\\nJr o\\nCL o\\n03\\nz .a\\n.c\u00c2\u00a3 0\\ns ss\\nO CL\\n\u00c2\u00a31- 0\\n03 O\\n00 o\\nk_- 0\\nC\\ns- ss 03\\n0 _ _\\nCL 0 P\\no c\\no3 c/3 q)\\na2\\ni\\n-rf 9 -Q\\nX -O 03\\n8 -g\\n5 cr\\n8-\\nCD\\nC 1\\n0 0\\ng3\\n03 O\\nw\\no\\no\\nO\\no\\nc\\n0\\nE\\n9.\\no\\nCT\\nQ- it-\u00c2\u00ae\\n0 c\\n0 C p\\n0\\nt;\\no\\nS O\\nQ. S\\nW\\nc c\\n0 _0 0 o\\nID H O\\nr-\\nf\\nC30\\nq\\nq\\nT\u00e2\u0080\u0094\\nP\\no\\nP\\np\\nP\\n03\\nCO\\nN.\\nin\\nCM\\nCM\\nY~\\nCM\\nYy\\np\\nYy\\nID\\nCM\\nq\\nq\\nCO\\nCM\\nin\\nO\\nq\\n00\\n03\\nq\\nq\\nY*.\\nCO\\nP\\nO\\np\\np\\nP\\nCO\\nCD\\njn\\nCM\\nCM\\n0\\nCM\\nYy\\np\\nP\\nCO\\nCo\\nCO\\nP\\nCO\\nCM\\nin\\n03\\nco\\nCO\\n00\\nq\\nco\\n0\\nP\\nO\\nP\\np\\nP\\n|Y\\nm\\n0\\n0\\nCM\\nN\\n0\\nCM\\nYy\\np\\nP\\nin\\nn\\nCO\\nP\\nCM\\nCM\\nin\\nS3\\n03\\nq\\nP\\nco\\nK\\n03\\nP\\nq\\nP\\nYy\\nP\\n0\\nin\\neo\\n00\\nCM\\nCM\\nS3\\nCO\\nCM\\nCM\\nP\\nP\\neo\\nT\u00e2\u0080\u0094\\nN\\nK\\nCO\\nYy\\nCM\\no\u00e2\u0080\u0098\\nCM\\nin\\nK\\nco\\nCM\\n03\\nCO\\nP\\np\\nCM\\nP\\nP\\n00\\nco\\n0\\nr-~\\nCM\\nCM\\nCO\\nCM\\nCM\\nP\\nP\\nCM\\nT\u00e2\u0080\u0094\\ni^-\\nK\\nCO\\nYy\\nCM\\np\\nCM\\nCO\\ncn\\nCO\\nco\\nq\\nK\\nCM\\nP\\np\\nYy\\nK\\nP\\nP\\nCO\\nT\u00e2\u0080\u0094\\nm\\nCM\\nCM\\nP\\nCM\\nCM\\nCM\\nP\\nP\\nCM\\nCO\\nP\\nCO\\nYy\\nCM\\np\\nCM\\nn-\\nCO\\nCO\\nq\\nO\\n00\\nP\\nP\\nP\\nSO\\nq\\nCO\\nO\\nCO\\nCM\\nCM\\n00\\n0\\nCM\\nYy\\nP\\nix\\nCM\\nO)\\nr-\\nP\\nco\\nYy\\nCM\\np\\nCM\\nSi!\\n00\\nin\\nCO\\nCO\\nq\\nP\\nq\\nK\\nCM\\nYy\\nco\\nCO\\nCM\\nCM\\np\\n0\\nCM\\nYY\\nP\\nN\\nfs\\np\\nCO\\nYY\\nCM\\np\\n03\\np\\nq\\nco\\np\\nO\\nfY-\\nq\\nq\\np\\nq\\nSo\\nCM\\np\\nin\\nq\\nCO\\nP\\nr-Y\\nCM\\nYY\\nK\\nP\\nK\\nh-\\nP\\nCM\\nYY\\nCM\\np\\n03\\nq\\n1\\np\\nq\\nP\\na\\nco\\nCM\\np\\nq\\nP\\nfx\\nCM\\n0\\nCO\\nm\\nCM\\nCO\\np\\n0\\nCM\\nP\\np\\n03\\np\\nco\\nY\u00c2\u00bb\\nYY\\nCM\\np\\nCM\\nin\\nq\\n03\\nP\\nq\\nK\\nCM\\nCM\\nP\\nq\\nP\\np\\nCO\\nT\u00e2\u0080\u0094\\nq\\nin\\nCM\\nco\\nP\\nco\\nCM\\nq\\np\\nT\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094\\n03\\nr-.\\nP\\nco\\nYy\\nCM\\nP\\n00\\n03\\nco\\nCO\\nP\\nT~\u00e2\u0080\u0094\\nYy\\nr-Y\\nCM\\nP\\nq\\nY\u00e2\u0080\u0094\\nCM\\n03\\n0\\nP\\nin\\nCM\\nCO\\nP\\nY\u00e2\u0080\u0094\\nP\\nP\\n(O\\nCO\\nr^-\\nP\\nco\\nY^\u00c2\u00bb\\nYy\\nY\u00e2\u0080\u0094\\nP\\nq\\nco\\nq;\\nq;\\nq;\\nP\\nco\\nq;\\nq\\nq\\nq\\ns?\\nO\\nz\\np\\nin\\nin\\nZ\\nZ\\nZ\\nY\u00e2\u0080\u0094\\nP\\nfY.\\nco\\nZ\\nZ\\nZ\\nZ\\nIX\\np\\nCM\\nCO\\nP\\n00\\nq;\\nq:\\nq;\\nP\\nq\\n\u00e2\u0096\u00a0q\\nq\\nq\\nq\\nIT;\\n03\\nz\\njn\\n10\\nq\\nq\\nZ\\nZ\\nZ\\nq\\nq\\np\\nCM\\nZ\\nZ\\nZ\\nZ\\nSP\\nCM\\nCM\\nCM\\nP\\nq\\nq;\\nq;\\nq;\\nK\\n03\\nq\\nq\\nq\\nq\\np\\nCO\\nz\\nN.\\n0\\nZ\\nZ\\nZ\\nR\\nCO\\nZ\\nZ\\nz\\nZ\\nYy\\nP\\nCO\\nCM\\nNT\\nQ. ID\\n0\\n0\\n0\\n0\\no\\no\\nol\\n0\\nk_\\nCO\\n13\\nT3\\nC\\nz\\no\\np\\np\\nK\\n6 Uj\\ns c!\\nCO\\n\u00e2\u0096\u00a0Q 03\\n0 C\\n\u00e2\u0080\u00a2c S\\n03 9- O\\nC o\\nc\\n03 O\\n0\\n0- o\\no\\n0\\no\\n\u00e2\u0096\u00a0O\\no\\no\\n0 0\\n\u00e2\u0096\u00a0E\\n0 -C\\n93 8\\nL.\\n0\\n-C SZ\\n2 111\\n0 P\\nt:\\nCL 0\\n0\\nI S\\n\u00e2\u0080\u00a25^ Pp\\no\\n0\\nt\\n03\\nF O\\nn l. 0\\nX. 0 Q3\\n5 o\\n03 o r_\\nc\\n-c\\nE\\n0\\nCL\\nL.\\n0\\n0\\nCL O\\nAppendix A National Emissions (1970 to 1998) A-13", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0213.jp2"}, "214": {"fulltext": "National Air Pollutant Emission Trends 1900-1998\\n\u00e2\u0096\u00a0o\\nD\\n3\\nC\\nc\\no\\nCO\\nI\\n0\\nn\\n(0\\nI-\\no\\nCT|\\n1\\n4-^\\nQ\\no\\n0\\no\\nl_\\n3\\no\\nw\\nC\\\\J\\nc\\\\j\u00e2\u0080\u0098\\nCM CM\\nTt 0\\nCM*\\n03 CO\\n00 JO\\n00 CO\\ncm\\ny- CD\\n00\\nCO q\\ncm\\nCD CO\\nT\u00e2\u0080\u0094\\n0- q\\nCM~\\n10 03 CM\\nyy CO Cm\\nCM O\\nCO 3\\nCD q\\ncm\\n0 co\\nfY\\nin co\\ncm\\ny- q\\nCM \u00c2\u00a3s\\nm co\\ncm\\nCO o\\nCM 03\\nm co\\ncm\\n(Q O)\\nt- io CM\\nCO o\\nT~ co CM\\nq q CD\\ny~ co cm\\nq }p r-\\nK CM\\nin |p\\nco\\nCD co\\ncm\\nCO CO\\nq CO\\nCO CO\\ncm\\n05 ;c;\\nq CO\\nin co\\ncm\\nin jo\\noo co\\nCD\\nco\\nI\\n0 q\\nCD\\nCM*\\nO CM\\nis. 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CO\\nCCS OS\\no .2\\no -S\\nas\\nt S\\n3\\nw\\nco y\\n0\\nO -5=\\nc s\\na I c s=\\n_ W\\ncd cd S,\\na O) 2 1 2\\n(J 3\\nS 5\\n3 3\\n\u00e2\u0096\u00a0u m cr -J\\nq. 5 5 cq\\no o\\na a\\n0) CD\\nE E\\nE\\nO\\no\\no\\na\\no\\nO\\np CO\\nt (O\\ncd .Q.\\nQ- -c\\no to cfc\\n2 5\u00c2\u00b0\\nCD\\no. a\\nQ.\\nO\\nO\\nO\\n03\\nt\\nCD\\na\\na\\nq5\\nE\\nE I\\nI\\ncj\\n__ co\\nCD E\\ng) J)\\nCO\\nCD\\n.C\\n8\\nC CD\\na o\\n3: c\\nCD CD\\nE c\\nr CD\\na a\\nE 1 g\\ncd -is E\\nCD\\n.c\\n-2\\n8\\nc\\no\\na\\nCD\\nl.\\nCD\\n-c\\no\\nQJ\\no\\n.co\\nP o ,o\\n2\\nc\\na CD\\n-S\\nt- -C -3\\nOOO\\n3 s a\\nCD fc\\n8\\no\\nCD\\nc\\nos a\\nCD yS\\nC CD\\nCD o\\nC CO\\nD\\na\\nc\\n2\\no\\nCO\\nCD\\nc\\nc\\na -c\\n-S ID c= i=\\nCD CD E\\nCD\\n*k_\\n3\\nD\\nC\\n5\\nsz\\n3\\nc\\na\\n2\\no\\n.co\\nas\\nE\\nCO\\n,o\\nCO\\na\\nQ.\\no\u00c2\u00abS\\ns.\\ngs v.\\n-o CD\\na -c\\n-q\\nc o\\nA-14 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": 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M- O CM C\\\\J\\nCM CM\\n(0 C\\\\|(OlOCMCMOOO OTtCMOCOOCJ)p\\nO CO\\nO CO\\nO yT\\nCM\\nCM\\nCM\\ncm N\u00c2\u00bb\\nCM K\\nCM K\\nNO) TOCOCO^\u00e2\u0080\u0099rOr-IOO\u00e2\u0080\u0099 r TOCOCOoCO tlOCgO OCM rCMinCO^MCMCMlO\\nCOO) CO^lO iOU) lO Co CO 4\u00e2\u0080\u0094 CM CM C\\\\J CO CM CM CM CO\\n00 ^CMCOO N\u00c2\u00bbCO lo CM ^4\u00e2\u0080\u00944\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094 4\u00e2\u0080\u0094 T-T\\n4tO)4rc\\\\|ioo r^cicM oo TO^coin f\u00e2\u0080\u0099 io o(NO 0 T!oinco4 CMCoin\\nC00) O TC)SS^in\u00e2\u0080\u0099 IO CO CO 4 CM CM CM CO CM CM o- cm CO\\nCO T C\\\\|COO C COCO C CO CM y- 4\\n,_r 4 \u00e2\u0080\u0094r\\n(0 -C NlflV) r rK(0^!0*-ff^OCMCMC0C0C0M00(O44O4-^2(DC0*- Cci fl0\\nC00) 4- 0-C0 0-0\u00e2\u0080\u0099-- X t CO CM CM CM CM CO CM CM M- CMCO\\nfv44 (\\\\lOO NcD crv r\\\\i 4\\nCO CM\\ncNjcp^-^^^K^ipr^-CMO)\\nOCM M- C0 N.^4~C0\\noco c\\\\i M- -0)m\\nCOfO^co^^lo^^coCOO\\nCM N r CO^-\\nco\\nCO\\nCO\\nT*T\u00e2\u0080\u0099OOC0CDC0C010C0C0CM t -CMC04TC0t-OCMC0C3OC0\\nM-CMO M- M- M-CO cm CO CO\\nM- CO T\\nM\u00e2\u0080\u0099^rOOC0inC\\\\| M M tC\\\\|CMCMC04rCM4jC\\\\|C0(04 C0 t\\nCO CO 4 Co M Co CO Cm CO 4-CM CO\\nCO CO y~\\nCM\\nr^o- o- 2;^co ina3\u00e2\u0080\u0099~o-\\n(00 C| -CO t O)U)\\n4r^4rO)Oo^coCRCMCO\\nQCOO tCO \u00c2\u00bbCO\\nlO CO 4~~\\nCMCO TCOCMCOOCOCMCOCM\\nCm 03 CM CO Cm\\nV\\nTO\\n3\\n.c\\n\u00e2\u0099\u00a62\\nc\\no\\no\\nc\\nsi to\\nt- -c\\nI\\n-J\\no\\nVi\\nTO\\n-c a=\\ncl to\\nTO -C\\nTO cl\\nMe w\\no TO\\n5 TO\\n3 S\\no o\\nc\\no\\n1\\nTO\\nO\\n.o\\no\\nQ)\\na\\nCO\\n.1\\nCO\\nTO\\nTO\\nTO\\nc\\nTO\\no\\nTO\\n1-\\nTO\\nE\\n3\\nTO\\nc\\no\\no\\nTO\\n\u00e2\u0096\u00a0c\\nTO\\nx:\\nK\\noc\\no\\nI\\nI\\nUj\\no\\ns\\nOc 3\\nO CD\\nt-\\nCO\\nTO\\nc\\nTO\\nCL\\n\u00c2\u00b0CS\\n_OT\\nTO\\nc\\nE\\n.TO\\nTO\\no\\nTO\\na\\nTO\\nl-\\nO TO\\nIs\\nC TO\\n03 5\\nc -Q -g\\n4^ .TO S\\nTOC.\\nO TO HS\\n5= i. TO\\nc\\na\\nO\\nc\\n3\\ns\\ns\\n\u00e2\u0096\u00a0jjj\\nc\\n3\\nTO\\n.c\\no\\nTO\\nTO\\no\\nTO\\ns\\n3\\no\\nW V.\\nTO TO\\nTO -C\\nTO\\n03\\nTO\\nL_\\no\\nCO\\no\\n3\\nTO\\no\\nE\\n3 TO\\nTO C\\no\\n\u00e2\u0096\u00a0c\\no\\nCL\\nw\\nc\\nTO\\no\\nTO 1\\nCL O) O\\nO O\\nESS\\nJ TO TO\\no\\nTO\\nI f.8\\nTO\\n3\\nMj 4- (S\\nO) o 2\\nTO 3\\nTO\\no o\\ns s\\nO) o\\no\\nTO 3\\nTO 3\\nO) TO\\nTO\\n,c\\no\\nTO\\na\\n03\\nTO\\nTO -2\\nTO 2\\nO\\ncx TO\\nTO TO\\nTO O i: h:\\nTO\\nCL\\nTO TO\\n03 03 to TO\\n.C .C c/3 TO\\nTO TO\\nC5 O\\nTO TO XS\\nTO TO -O\\nTO TO TO\\nv.\\nTO TO S:\\nO\\n3\\nO\\no\\nE\\n3\\nTO\\nO\\nTO\\nCL\\noS\\nE\\nI s\\nI s\\nTO\\nCL\\n1\\n*s\\n8-\\n\u00e2\u0096\u00a0O\\nTO _\\nS 5\\nI\\nTO\\nTO\\nO\\n3\\n\u00e2\u0096\u00a0o\\n-C -C\\nTO y TO\\nO TO O\\nC X3 C\\n03 O) 03\\nC C C\\n6 6 6\\nTO TO TO\\n2 2-2\\nTO TO TO\\n\u00e2\u0080\u00a22 -2 -2\\no o o\\nTO TO TO\\na a a\\n03 03 03\\n3\\nTO\\nTO\\ng3 03\\nTO TO\\nE eg\\n\u00e2\u0096\u00a0e o\\nTO\\n\u00c2\u00a73\\nTO O)\\n.C\\no 6\\nTO\\n03 O\\nc\\n6 TO\\nTO TO\\n-2 8\\nTO\\nTO\\nC\\no\\nTO\\n\u00c2\u00a73 E\\nTO\\nTO -C\\nAppendix A National Emissions (1970 to 1998) A-15", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0215.jp2"}, "216": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n~G\\nG)\\n3\\nC\\n-3\\nC\\no\\nCO\\n0\\n-Q\\nCO\\no\\ncr(\\n(U\\n\u00e2\u0096\u00a04-\\no\\n0\\no\\nL.\\n3\\no\\nc/i\\nO O tJ- CD in\\ncm o Tt eg\\nco -m-\\nO O) (D Ifl\\nCM O O CM\\nCO\\nw s co co in\\n05 tj- cm\\nCO CO\\nr- n- h~\\nto oo in co\\nCO \u00e2\u0080\u00a2M\\nCM N in O) N\\nCM CD in CO\\nCO o-\\nO) CO O) N\\no m m co\\nco o-\\nCO CM CM CO CO\\no in co\\nCO o-\\no^ocMm l oc pooococoo ncM^o ?)inco^r^cM l o l ocM\\ncomo c\\\\|Ni incMMcoco 2 )n\u00c2\u00aecoT-coNincnp\\nCM 0 00 N O D N CM M\\nlO CM CM\\nCM\\nO f ^CMCO l OOCOC)a)0)CMCMCT)OCO ~CO|^QOO)CMTtKlnCM\\ncm in o c\\\\)(O itT-^cocMC)roS)cnr-c\\\\|C 0 SMC i\\nCM CO N K O CO CM CM CM\\nm CM CM\\nCM\\no Cp T- o\\ncm in o\\n2- CM\\ninooKooaoaocMCMao\\nCO T\u00e2\u0080\u0094\\nOinPcoocoKcocococnCM\\nCOCM\u00c2\u00aeNCOCOCD J^O)CD t T\\nM- CO CO o 05 CM CM CM\\nco cm cm cm\\n13\\n05\\n3\\n.c\\n\u00e2\u0080\u00a2w\\nc\\no\\n4j\\nK\u00c2\u00bb\\noc\\no\\nI\\n1\\n08\\nUj\\n(3\\n2\\ns\\nV)\\nN Tf co O\\n7 co in o\\nCl CM\\nCOOT-COCOinCO^-CD l n\u00e2\u0080\u0099~CT)COCOr^O)CM M- M-\\nNCMinT-CUNCOPCM\u00c2\u00ab fCMO)ncM--2\\nv- CO K 7 co ffl co N CO CO CO\\nCO co co \u00e2\u0080\u00a2r-\\noincoinocM CMDNoin\\n7 3 D o Kciim^ioajco\\n3 cm m\\noo\\nC3 -st-\\n\u00e2\u0096\u00a0M- r~-\\nCO co CO\\nKoCnCOMT-COM-CO\\nr CooooT-co Y\\nO) O O) Tf CO CO\\nCO0N^Oj-\u00e2\u0080\u0099 OO)COMCOCOCM^3NCnCM0OO COCO\\n7 2- K O N^ini-fflN(0 i -KCO^KKcilr-0\\nCo CM in 00 N CD CO CO CO CO\\nCo co co T-\\nO CM\\n2\\nZ 5\\nco tooiocooirooi\\nm o\\nCM\\nCO CM M\\nCO CD CO\\nin\\nCMCMCJ)C0C0O5O)^cX)CMC0C0\\nK.COPCOCO M-COCO-r-O\\nC3coK in CO K CO CO CO\\nco co co T-\u00e2\u0080\u0098\\nin o\\ncn co in co\\nCM Cl\u00c2\u00ac\\nin 00 T- o CM\\n0)00 tOl50N\\n7 5 in O co CM -M-\\n05 cm\\noo\\nT-CD 00 3 O 5 COKc 0 CO\\n05CDCMC3cOCOCOCOC\\nm o o\\nco 7 V\\nCO 05 M- CO CM\\nCM i- O T\\n(D O) K M CO Co\\nO CO CM O O O O\\no co in co r-\\nC0 -M-\\nCM\\nCO 00 CD M\\n7 5 M- O)\\nCO T-\\nO) co cd o)\\nCo -\u00c2\u00ab3- -T-\\nDM DCOfslOCMCMQCMCMCM^COCO\\nCODCM^M-COCOCUCOCOCOi-O) T\\nin co 05 co d O) 0 m- co cm\\nco co co T-\\nCO 1 CM CD in\\nCM -M- in CO 1\\nCM O-\\nCO CM CM I s CD\\nCM CM in CO T-\\ncm m\\nn in ro n\\nO CO M CO i\u00e2\u0080\u0094\\nCM O-\\n000 0 0 c\\\\|( 0 ff\\n7 3 m N cp\\n05 CM Cm\\n000 0 0 1 OCMK T\\n7 In CD 00 K\\nQ} r\\\\ 1 r\\\\ 1\\nCM\\nCM\\nCMinOOOlNCllONCOCDNOCMCD\\n05 OiCD T l ncD r M-T- \u00c2\u00ab^-CO\\nin -\u00c2\u00abt to o co m co co\\nN, tJ- i\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nCMCMOoOrococooincofflinCMCMO\\nO \u00c2\u00ab3500COIOCM^COCM ^CO\\nCD C\\\\| T- T- O) (O CO CO\\n00 in co\\nCM\\n000 ?1 10)CO\\n7 N- CD O\\nCJ) co\\nCM o\\nO 1\\nco\\nO\u00e2\u0080\u0099\\n05\\nin\\nooco-M-OM-inKcocnoocMOo\\nKcD\u00e2\u0080\u0099~COCMCOCOi-r y CO\\nCO CO CO 7 M- 05 CO CO\\nO) in co\\nCM\\nCO\\nCD 00 7\\no- in\\nT- CM\\n00 O 7\\nO- CD\\nCO\\nz z z z z\\nco CD CM\\n^5 ID N\\nCO CO\\n22\\nR!\\nCO\\nCO\\nOPlNCD KDOO\\nCM^OM-COinCMCO\\n05 05 CO\\nCM CM CM 00\\nco in to\\nO Cm Co CO M-\\ncm\\n05\\nCO\\niP 00\\nz z z z\\n-.Kr-05 ~ooiv.^in T\\n2 M-r s N-oococominco\\nCo CM W CM O D n o\\no IS. K. cm T\\n10\\nCO T-\\nT- CM\\no- in\\ncd 3comm:m:^3\\nz^zzzzzg^^^ZS^zzzz\\nCMCOCOCOOM-COcOCDCOttit;\\nN\u00c2\u00ab05C0C0|v.C0OTtcDC0\\nN OCMSC jC l^^\\n05\\ncm cn 05\\nCM\\nO)\\nc\\nQ_\\nE\\nLU\\n08\\nO)\\nc\\n0 cn\\nO) 05\\nCO CO\\nCO CO\\nCO CO\\nc c\\no o\\n5 o3\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094\u00e2\u0080\u00a2\\nCO CO\\ncn cn\\ng g\\nt\\ncn cn\\nCO CO\\n\u00e2\u0096\u00a0c\\ncn cn\\n05 Q.\\nco 2\\nS 2 5\\nm W t\\nCO co\\nCO o o\\no E E\\nQ5 cn\\nCO SZ JZ\\nCO o o\\n\u00e2\u0096\u00a0c\\nCD o\\n9-\\n5\\n2 2 n\\nCO I\u00e2\u0080\u0094 05\\nCO CO\\nC5 O\\ng g\\nc c\\nCO CO\\nCD CD\\nn\\ng\\ncn\\nCO O O\\nE 03\\ncn cn jn\\n\u00e2\u0096\u00a0c x: co\\n0 0-3\\no g S\\nc c\\nCO co 2\\nO) uj\\n003\\nCO\\nC5\\ns\\n\u00e2\u0096\u00a0c O\\no Uj\\nCL Qc\\nCO\\nC \u00c2\u00b08\\nCO\\nl:\\nH 5\\n0 2 co\\nCO\\nk\u00e2\u0080\u0094\\n05\\nco\\nCO\\nQ5\\no\\no\\ni_\\no\\no\\no\\na.\\nCO\\nQ\\nti\\nCO\\ni\\nCD\\nc\\nc\\nl\u00e2\u0080\u0094\\n3\\nCD\\nco\\ns\\nc n\\nI\\n.co\\nE\\nco 9\\nc t\\nCO E\\nS S\\ncn\\n.CT3\\nI k\\n05\\nco\\n05\\n03\\n03\\nO Q.\\nE O\\n0\\n0\\nQ g\\nCO rn\\n05\\nlu\\nd\\n1\\nQ\\no\\noc\\no\\n08\\nco\\no\\no\\nCO\\n05\\naj 73\\n-2\\n95\\n05\\nCO\\nco\\no\\n9\\nJC\\nCD\\nCO\\no\\n3\\nCM\\n0\\n3\\nCO\\nco co\\nO) 05\\nCJ\\n2 c 5\\nCO\\nCO\\n05\\ng\\n!c\\n05\\nip\\n\u00c2\u00a75\\nCO\\nCO\\ng o\\nco\\n93\\nCO\\no\\no\\ns\\n3\\na\\nI\\nJC\\nCD\\nCO\\nCO\\n05 CD 0\\n\u00e2\u0096\u00a02 -2 3\\np p\\n9\\n-c -c\\n.CD .CD\\nCO\\n05\\nI\\nCO\\n\u00e2\u0080\u00a2SJ\\nC5\\n-5\\nI\\n05\\nco\\n05\\n3\\no\\n2\\n05\\nCO\\n05\\nt\\nI\\nco\\n05\\nA-16 Appendix A National Emissions (1970 to 1998)\\nlight-duty diesel vehicles", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0216.jp2"}, "217": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n-a\\n(1)\\nD\\nC\\n+3\\nC\\no\\nO\\n00\\nI\\no\\nn\\nco\\nI-\\n00\\n\u00e2\u0096\u00a0M-\\n12\\no\\nT\u00e2\u0080\u0094\\nco\\nT-\u00c2\u00bb\\nin\\n00\\nC5\\nC5\\nC5\\nIT)\\nY-\u00c2\u00bb\\n05\\n00\\nK\\no\\nco\\nCD\\nco\\noo\\nCM\\nCM\\nin\\nY\u00e2\u0080\u0094-\\nco\\no\\n05\\nY\\nY-\\nO)\\no-\\nr^-_\\nCO\\nY-\u00c2\u00bb\\nK\\nY\u00e2\u0080\u0094\\n0vT\\nT_\\nc-\\nm\\n12\\nO\\nCM\\nFN\\nN\\n00\\no\\nO\\nY-y\\nCD\\nY~-\\nIT)\\nY\\nco\\nD\\nCD\\noo\\n00\\nCM\\n1\u00e2\u0080\u0094-\\nCM\\nK\\nY\u00e2\u0080\u009c\u00e2\u0080\u009c\\n00\\no\\nY\\nY\u00e2\u0080\u0094.\\nO\\nin\\n\u00c2\u00b00_\\nN.\\nY*\u00c2\u00bb\\nK\\n^r\\nCM\\nT\\noT\\nT_\\nCD\\nT-\\nCM\\n12\\nO\\n12\\nY\u00e2\u0080\u0094\\nCM\\n05\\nCO\\no\\nC3\\nK\\nCsJ\\nY^\\nCO\\nY\\nto\\nCD\\nCO\\nCO\\nco\\n7-\\nCM\\nK\\nM\\nO)\\nY^\\nK\\nC\\\\J\\no\\nY\\nY\u00e2\u0080\u0094\\nCD\\nCO\\nCD_\\nr\u00c2\u00ab-\\nK\\nY\u00e2\u0080\u0094\\nK\\nTf\\nOM\\nT\u00e2\u0080\u0094\\ncm\\nT\\nm\\nO)\\nS2\\nM-\\n00\\nC3)\\nM\\nK\\nM\\nY~-\\nC5\\no\\nY-\\nY\\nCO\\nCD\\nC3)\\nCM\\nco\\nO\\nCM\\nCM\\no\\nY\u00e2\u0080\u0094\\nK\\nCsJ\\nO\\nY\\nY-\\nCD\\no\\nO\\nY~\u00c2\u00bb\\nK\\nCM\\nK\\nCM\\ni\u00e2\u0080\u0094\\nom\\nCM*\\nY\\n_\\nO\\nO)\\nY\\nCM\\nC5\\nY-y-\\nY-.\\nO\\npo\\nY\u00e2\u0080\u0094\\nO)\\nCM\\nCD\\nK\\nCD\\nco\\nM-\\nM\\nN.\\nM\\nC5\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nN\\n05\\nY\\nY-\u00c2\u00bb\\nCD\\nCO\\nCD\\nK\\nCM\\nK\\nY-y\\nr\u00e2\u0080\u0094\\nN\\n00\\nO\\nS3\\nM-\\nO\\nCM\\nCM\\nY-~\\nY\u00e2\u0080\u0094\\nO\\nPM\\nCO\\nY~-\\nY\\nCM\\nCO\\nCD\\nOM\\nm\\noo\\nM-\\n00\\n12\\nCM\\n05\\nY-Y\\nK\\no\\nO)\\nY\\nY\u00e2\u0080\u0094\\nCD\\nco\\nCD\\nT\u00e2\u0080\u0094\\nY^.\\nK\\nY*\u00c2\u00bb\\nom\\nCM\\nm\\nCM\\nM-\\nT~-\\nM-\\nT-\u00c2\u00bb\\nin\\no\\nC5\\n00\\nCO\\nY\\nO\\nC^\\nD\\nC3)\\nCM\\nCO\\nM-\\n00\\nco\\nCM\\nco\\nY y\\nP\\no\\n05\\nY\\nY\u00e2\u0080\u0094\\nCD\\nin\\nCD\\ne\u00e2\u0080\u0094\\nK\\nY\u00e2\u0080\u0094\\nK\\nY\u00e2\u0080\u0094\\nT\\nN\\no\\no\\nO\\nCM\\nco\\nY\u00e2\u0080\u0094\\n05\\nO\\nK\\nr^\\nY\u00e2\u0080\u0094\\nO)\\noo\\nCM\\nCO\\nO\\n00\\nYY\\nCM\\nK\\n00\\nO)\\noo\\nY\\nY\u00e2\u0080\u0094\\nD\\nin\\nCD\\nT\u00e2\u0080\u0094\\nK\\nK\\nCO\\nY*\u00c2\u00bb\\novT\\nO\\nin\\nCD\\nCO\\nO\\n00\\nO\\nO\\nY\u00e2\u0080\u0094-\\n05\\nY^.\\nQ\\nY\\no\\nY~.\\nY-.\\nO\\no\\nCD\\nT-\\n00\\nCM\\nO\\n00\\nO\\nCM\\nK\\nCD\\nco\\nY\\nY\u00e2\u0080\u0094\\nCD\\nin\\n00\\nK\\nY\u00e2\u0080\u0094-\\nK\\nCO\\nY\u00e2\u0080\u0094\u00e2\u0080\u00a2\\nT_\\no^T\\nD\\nOM\\no\\nO\\n00\\nCM\\nC5\\nM-\\nco\\nY-*.\\nO\\n00\\nY-*\\nC5\\no\\n00\\n1\u00c2\u00b0\\nO\\nCO\\nO\\n00\\nCO\\nM\\nCO\\n05\\n00\\nK\\nY\\nCD\\nin\\nCD\\nT\u00e2\u0080\u0094\\nCO\\nY\\nK\\nCO\\nY-*\\nT_\\nOM\\noo\\nN\\nCM\\nO)\\nin\\nin\\n05\\no\\n05\\nK\\nO\\nK\\nh-\\nY^-\\nY\u00e2\u0080\u0094\\nQ\\noo\\nCO\\nN\\nin\\nO\\nco\\nco\\nCM\\nin\\nY\\nr\\nN.\\nY\\nCD\\nin\\nCD\\nco\\nYy\\n00\\nCO\\nY*\u00c2\u00bb\\nom\\nT\\nin\\nom\\nCD\\nco\\nin\\nK\\nCO\\n05\\nK\\nin\\nY~~\\nO\\n05\\nCsJ\\nY\u00c2\u00bb\u00c2\u00bb\\nY\u00e2\u0080\u0094\\nCO\\nCO\\nco\\nT-\\n00\\nin\\nO\\nCO\\nY\u00e2\u0080\u0094-\\nY\u00e2\u0080\u0094\\n00\\nCO\\nCO\\nlO\\n00\\nCD\\n7-\\n00\\nT\u00e2\u0080\u0094\\nCO\\nYy\\nco\\nCO\\nY*\u00c2\u00bb\\nT\\ncsT\\no\\n0m\\nY\u00e2\u0080\u0094\\nC3)\\n00\\n00\\nK\\nK\\nin\\nY\u00e2\u0080\u0094\\nO\\nr^\\nY\u00e2\u0080\u0094\\nJQ\\nop\\noo\\noo\\nin\\n00\\nCO\\n00\\nCM\\n2\\n00\\nCsJ\\nco\\nCM\\nCD\\n00\\ni^-\\nin\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\noo\\nCO\\nT-~\\no\\nCT\\nD\\no\\no\\no\\nkm\\n3\\no\\nco Y C\\\\J\\nCM\\nCM\\nco co\\nD~ CO CO\\nCO CO CM O O Co\\nI s CO CM\\nco (o n f\\nC--- Y CM\\nf CO\\nCM\\nco Y in\\nCM\\nO CO CM\\nCo N M O Cm Co\\nr- co cm\\nCO O CM O CO\\n00 CO CM\\nCM\\nCM\\nn\\nCM T-\\n5\\no\\nCm\\nyi\\nUi\\n-J\\no\\n5\\nQ\\nz\\n2\\nUj\\no\\ns\\nQ\\no\\ncc\\no\\n2\\na)\\nc\\no\\n1/5\\nCO\\n0\\nT3\\nCO\\no\\ncc\\nI\\nc\\no\\nc\\n0)\\nC 73\\n\u00e2\u0080\u00a22\\nco\\nO .co Co\\n2 S 03\\nw 3 C\\nts\\n8 -2-2\\n.co\\n2\\nCD\\nll\\nCD\\nO\\nCD\\no\\ne\\nCO\\nc\\nCD\\n2\\nCD\\nCO\\nCO\\nCD\\nC\\nc\\nco\\n2 CD\\nC CO\\n3 g .2\\no Q\\nB ill\\no\\nCO\\nc\\no\\n05\\nc\\n,o\\nO CO\\n2 c\\nc\\nI\\nco\\no\\n2 e 5\\n0 C\\n-8\\n8 .c\\n.co\\n2\\nCD\\nE\\n1\\no\\no\\n-c\\n.O)\\n2\\nCD\\nCO\\nCO\\ng\\nCD\\nO CD\\n-2\\n2 c\\n2\\nE f\\nI?\\nCD\\nO\\no\\no CD\\nCO c c\\n2 .5\\n2 Jo\\n2\\n2\\nCD\\n0\\nCO\\nCD\\n___\\nCD To\\nY O O O O\\n2 co\\nY 00 O C5 C5\\n2\\nCO 05 o o o\\nY\\n05 O C5 O\\nY\\n00 CM O O O\\nm\\nCO M O O O\\nin\\n00 CM O o O\\nin\\nN CM O O O\\nm\\nO) CO Cel\\nCMincO\u00e2\u0080\u0099 COCM T\\n00 CM C| 2\\ncj m cm o m;\\nCO CM Cl\\n1\\n0)loaKK J -^0 rCMN\u00c2\u00bb COC\u00c2\u00bb)\\\\tO (Cl\u00c2\u00aeQM:M;(OCDOCO\u00e2\u0080\u0099\\nco y cm cm y cm 3\u00c2\u00bb co m a CM o\\nCO t- in c K CM T-\\netCnKIO OlOClQcr ONC f\u00c2\u00aeCOCN OO^^NNOCOO^\\nCO CO CM C| Y Cp 00 C3) 00 00 CD\\nLO T- C-O T Os. 1\u00e2\u0080\u0094\\n\u00e2\u0080\u00a2q; cm o o o\\n2\\ny i- o o o\\n5\\nY D-. o o o\\n2 00\\ncc n o c(\\n2 n Z Z\\nY o o; -q;\\n5 CM S Z\\nm; cm o m: m:\\nZ OM S Z\\no\\n3= CD\\n2 .c\\na O\\n|8|\\nO C O)\\nQ)\\nCO\\na)\\nSZ\\n6\\nV. -g\\nw 5\\nc\u00c2\u00a3 o 4-\\no C\\nCO o\\ncc z\\nCO\\nCO CO\\n(0 Oi)\\nTo\\n1\\nCD ^o\\n75 c\\n03\\nQ) 0)\\n(3 CO\\nco\\n^3 CD\\n0 k\\n2 2\\n3 C\\ni\u00c2\u00a7 8\\nAppendix A National Emissions (1970 to 1998) A-17", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0217.jp2"}, "218": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n\u00e2\u0096\u00a0o\\nD\\n3\\nC\\n3\\nC\\no\\nO\\nCO\\nQ)\\nn\\na\\nCO\\n\u00e2\u0096\u00a0o-\\nCM Tf\\nT- CO\\nT _\\no\\nD-\\nCT)\\nT-\\nCM\\nT\u00e2\u0080\u009c\\nCT)\\nN.\\nCD\\nT\u00e2\u0080\u0094\\n^5-\\nO) CO\\n0 lO\\no\\nco\\nCT)\\nr\u00e2\u0080\u0094\\n1\\nO)\\nD~\\ncd\\nCM\\n\u00c2\u00b00\\nT_\\nT-\\nco\u00e2\u0080\u0099\\nT\u00e2\u0080\u009c\\nco\\nO CM\\n1 lO\\no\\no\\nco\\nCT)\\nTf\\nCD\\nCO\\n05\\nCT)\\n00\\nD-\\ni\\noo\u00e2\u0080\u0099\\nT_\\nIf)\\n\u00e2\u0096\u00a0O\\nr- f\\nd~ ^r\\nCM\\no\\n1\\nO)\\n1\\nCO\\nT**\\nO)\\nio\\nCO\\nCO\\no\\nCM\\n^r\\n\u00e2\u0096\u00a0O\\no co\\nr- fr\\nCM\\no\\nCO\\nO)\\nT\u00e2\u0080\u0094\\nCM\\no\\nco\\nO)\\nK\\nco\\n1\u00e2\u0080\u0094\\nCN\\nCO\\nN\\nCO CO\\ny _\\no\\noo\\nO)\\ny~-\\nO\u00e2\u0080\u0099\\nCO\\nO)\\nco\\nLO\\nCO\\n1\u00e2\u0080\u0094\\no\\nCM\\nCN\\nCO CO\\nO\\n^_\\nCM\\no\\nO)\\nO)\\nco\\nh-\\nto\\nO)\\n\u00e2\u0096\u00a0o-\\nt\\nco\\nT\u00e2\u0080\u009c\\no\\nCM\\nT\u00e2\u0080\u0094\\nco CO\\nCO\\no\\nCM\\no\\nCM\\nO)\\nT\u00e2\u0080\u0094\\nIP\\no-\\no\\nO)\\nK\\nT\u00e2\u0080\u0094\\nr--\\nCM\\no\\nD\\nCT) CO\\nO) Tf\\nO\\no\\nCD\\nCT)\\nT\u00e2\u0080\u0094\\nIf)\\nCO\\nO)\\nCO\\no\\nCD\\nT\\no\\nCM\\nO)\\nCM\\nCO\\nco\\nCD\\nz\\nS 2\\nCO\\nz\\nz\\nLO\\nT\\ncm\\nCM\\nCO\\n\u00e2\u0080\u00a2q;\\ns\\n2\\nT-\\nCO\\nco\\ncn\\nz\\nCp 7\\nCM ,c:\\nCO 2\\nCM\\nz\\nz\\nO\\nCO\\n,,_\\n\u00e2\u0096\u00a0rZ\\n0\\nCM\\nco\\nto\\no\\n00\\nco\\nO)\\nz\\nCO \u00e2\u0080\u00947\\nIf) z\\nCO\\nCO\\nz\\nz\\nCM\\no-_\\no-\\nCM\\no\\n2\\no-\\nCD\\nco\\no\\nz\\n$2 Z\\nCO 2\\nz\\nz\\nz\\nCO\\nco\\nr-\\nyS\\nco\\nCM\\nID\\nco\\nCD\\nCT)\\nO)\\nz\\nT\u00e2\u0080\u0094 \u00e2\u0080\u0094r\\nK z\\nz\\nz\\nz\\nz\\nO\\nT*\\nco\\nCM\\no\\nr-\\nz\\nCM\\nO)\\nz\\nS 2\\nO Z\\nz\\nz\\nz\\nco\\nCT)\\ny-T\\no\\nCO\\n0\\n0\\n0\\n0\\nGC\\n~s\\nP\\nc\\n0\\nCO\\n0\\nf\u00e2\u0080\u0094 ~o\\nLLl\\nUj\\no\\n0\\nC0 o\\nC\\nO o\\nO\\n0\\n0\\nL_\\no\\ncc\\nQC\\nUL\\n(f)\\n0\\nk_\\no\\n3\\nP \u00c2\u00b03\\n_Q o\\n0\\n5\\no\\no\\nCT\\nO\\niy 0\\nIf\\no 2\\ni- 0\\n0 0\\nr~ 4\\n=3\\nCO\\n0\\nTO\\no\\n0\\nCO\\n-J\\n1\\no\\n\u00e2\u0080\u0099c\\n0\\nCT\\no\\n1 3\\n-~j CT\\nH o\\nUj c\\n0\\nCO\\n_c\\n0\\nF\\nCD\\n_C\\no\\nQ\\n0\\n*5)\\n_l\\n_l\\n_l\\n0\\n0\\nO CD)\\nX c\u00c2\u00b0\\n0\\no\\nD\\nCT\\nK-\\no\\no o\\nI\\no\\nLL\\nF\\nO\\n3\\nO\\n2\\nF\\n0)\\nk_\\nO\\nE\\nCD\\nJZ\\nCT\\nCD\\nC\\nca\\n4\u00e2\u0080\u0094\\nc\\no\\no\\n0\\nk_\\n03\\n3\\n-Q\\n0\\n0\\n\u00e2\u0080\u00a2D\\n0\\n*0\\n0\\n\u00e2\u0080\u009cO\\n0\\nk_\\no\\nE\\n0\\n03\\n0\\n_Q\\n_0\\n03\\nO\\nc\\n0\\nk_\\n03\\nlO\\nCO\\nCD\\n0\\n0\\nl.\\no\\nO)\\n0\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094 1\\n03\\nO\\n0\\nO\\no\\nn\\no\\nCN\\nO\\nO)\\no\\n8-5*\\n5 5\\nCD\\nO)\\nc\\nO\\n0\\n*D\\ncn\\n0\\n\u00e2\u0080\u0099c\\nQ_\\nc\\n0\\nc\\n\u00e2\u0080\u0099o\\n0\\n-Q\\n0\\no\\nD\\nc\\nk_\\nD\\nJD\\n0\\nJD\\n0\\nv_\\n0\\n~o\\n0\\no\\n0\\nO\\nZZ\\no\\no\\no\\nO\\nw_\\nQ_\\no\\n0\\n[0\\n4\\n\u00e2\u0080\u0098k.\\nQ.\\nC\\n3\\nC\u00e2\u0080\u009d\\nk_\\n0\\n0\\nC\\n0\\n0\\nO\\nsz\\n0\\nk_\\nD\\nO\\nO\\n0\\n0\\n0\\n0\\nC\\nO\\n0\\nc\\nE\\nO\\no\\n0\\n0\\nk_\\n*0\\nn\\n0\\n0\\no\\n0\\nc\\nE\\nE\\nc\\n0\\nTD\\n0\\nT2\\nkJ\\n0\\nC\\n3\\n0\\n0\\n0\\n0\\n0\\nO\\no\\n0\\nE\\n0\\n3\\nk.\\n0\\nO\\no\\no\\n4\u00e2\u0080\u0094\u00c2\u00bb\\n0\\n0\\nC\\n0\\n0\\nd:\\nO\\nJZ\\n+4\\n4\\n4\u00e2\u0080\u0094\\n0\\n0\\n0\\nt3\\nE\\n5\\no\\n0\\nC\\no\\nO\\nd:\\ncn\\n\u00e2\u0080\u00990\\no\\n\u00e2\u0080\u00990\\n0\\nCT)\\nk_\\nD\\no\\n0\\nE\\n0\\n0\\n0\\n4\\nCD\\nCT)\\n0\\n0\\nLO\\n\u00e2\u0080\u0099CT)\\n0\\nk_\\nc\\nc\\n0\\n00\\nO)\\nO\\n0\\n*0\\n_c\\nin\\n4\\nc\\nk_\\nc\\n0\\nO\\n0\\n0\\ng\\n0\\nO\\n0\\n0\\nco\\nk_\\no\\n0\\nCD\\nLL.\\n0\\n4\u00e2\u0080\u0094*\\nc\\n0\\nE\\n0\\n0 co\\ns 2 .9\\nllo\\nto 0 CD\\n00\\n\u00c2\u00b03 0 \u00e2\u0080\u0098tO\\nO 0\\nC Olu\\nII\\nS 0\\n\u00c2\u00abc- cd\\n0\\no\\no D 0\\n0 0*-.\\nQ.\\n0 0\\n0\\n0\\n0\\nJ 5\\n5 -2 0\\nCD TO\\n2 o O\\n0 O\\nN z\\nA-18 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0218.jp2"}, "219": {"fulltext": "Table A- 4 Sulfur Dioxide Emissions\\n(thousand short tons)\\nNational Air Pollutant Emission Trends, 1900-1998\\nCO\\n02\\nr-\\nCM\\nCO\\nCD\\nCM\\n3\\n02\\nCO\\nC\\\\J\\nt\\n02\\nr--\\ni\u00e2\u0080\u0094\\nC3\\n02\\nuo\\nCM\\nK\\nCD\\nCO\\nCO\\nto\\ncm\\nY\u00e2\u0080\u0094\\nCM\\no\\nY\\nCD\\nCD\\nCO\\nN\\n02\\n02\\nT-\u00c2\u00ab\\nC\\\\J\\ni\u00e2\u0080\u0094\\nCD\\nCD\\ncj-\\nCD\\n02\\nY\\nCO\\nCD\\nM-\\nLO\\nCD\\nid\\nTt*\\nCM\\n\u00e2\u0096\u00a0r\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094\\n3\\nr-\\nCD\\ni\u00e2\u0080\u0094\\nCM\\nCM\\n3\\n02\\nCO\\nco\\ni\u00e2\u0080\u0094\\n00\\n02\\nCD\\ncj-\\nT\u00e2\u0080\u0094\\n02\\nK\\nco\\nCM\\nD\\n\u00e2\u0096\u00a0M-\\nCO\\nCO\\nT\\nId\\nui\\nCD\\nY\u00e2\u0080\u0094\\nT_\\nO\\n02\\no\\nCD\\n\u00e2\u0096\u00a0M-\\n02\\n02\\nC3\\n02\\n3\\nCM\\nK\\ni\u00e2\u0080\u0094-\\nCD\\nCD\\nCM\\n02\\n02\\nCM\\nCD\\nM-\\nCO\\nCO\\ni\u00e2\u0080\u0094\\nCD\\nid\\nCD\\nY\u00e2\u0080\u0094\\nT\\n02\\nCD\\nCM\\ncj-\\nCD\\nCD\\nM\\n00\\nO\\nK\\nCM\\nCD\\ncp\\nr\u00e2\u0080\u0094\\n02\\nCM\\nD\\n\u00e2\u0096\u00a0M-\\nJ-\\nK\\nT_\\nco\\nid\\nCD\\nT\u00e2\u0080\u0094\\no\\nCD)\\no\\no\\n0)\\no\\nk.\\nD\\no\\n0)\\nK\\nCO\\n3\\n3\\n3\\nCM\\n3\\nT\u00e2\u0080\u0094\\nCM\\n3\\nJ-\\n3\\nCD\\ncm\\n3\\nCM\\nT_\\n3\\nCM\\n3\\n3\\n3\\n02\\nS-\\nJ-\\n3\\n3\\n3\\nLO\\n\u00e2\u0096\u00a0D-\\nM-\\n3\\nCD\\ncm\\n3\\ncm\\nT\u00e2\u0080\u0094\\nY-\u00c2\u00bb\\n3\\nJO\\nCD\\nCD\\n3\\n3\\n3\\n3\\n3\\n3\\ncm\\ncm\\n3\\nCM*\\ni\\n3\\nCD\\n3\\n3\\n3\\n3\\nO\\n3\\n\u00e2\u0096\u00a0M-\\n3-\\n3\\nCO\\n3\\n3\\n3\\ncm\\nyS\\n3\\n3\\nT_\\n3\\nCD\\nT~-\\n3\\n\u00e2\u0096\u00a0M-\\n3\\n\u00e2\u0096\u00a0M-\\n3\\n3\\n3\\nCD\\n3\\n3\\n\u00e2\u0096\u00a0D-\\no co\\n3 3\\nrv. i\\\\\\noo y\\noo co\\nY Y\\nCD 3\\nCO CO\\nY Y\\nCO 00\\nT- O\\nY Y\\n3 C\\\\1\\nCM\\nLD CO\\nY CM\\nCM\\nCD Y\\nCO CO\\n3\\nCM\\nO CM CO CD CO\\nCO CM CO Co\\n\u00e2\u0096\u00a0O\u00e2\u0080\u0099 O\\n3\\n3\\nD-\\nCO\\n3 3\\n3\\nTj*\\nLO\\nI\\n3\\n3\\nCM\\n3\\n3 t-\\n3\\nCT\\nI s\\n3\\ni\u00e2\u0080\u0094\\n3\\n3\\nCM\\nO Y 3\\nt\u00e2\u0080\u0094 K. 00 CO\\nO)\\n3\\n3\\nO\\n3\\n3\\nTt CO\\nK\\n3\\nO\\n3\\n3\\nCM\\n3\\nCO f-\\nN.\\n3\\nco\\n3\\nT-\u00c2\u00bb\\n3\\n3\\nCO CO\\n00 Y\\nT- CO\\nO Y\\nCD O Co CO Co\\nO Q\\nCM\\nCO CO CD CM\\nCO CM\\n3\\nco\\nCO 02 CO K\\nco CO\\nCO\\nco\\nlO f\\nCD CO co CO\\nY 3\\n3\\nK\\nN\\n3\\n3\\no\\nh- N.\\nT~-\\nCD\\n3\\n3\\n3\\nt- 3\\nco\\nCO\\n3\\n3\\n3\\nr-\\noo\\nco\\nCO\\no y r-\\nco\\n00 CO\\nCM 3\\nr^- o\\n00 co K\\nJP\\n3\\nT\u00e2\u0080\u0094\\nY~~\\no\\nco\\nh-\\nCO\\n3\\nO\\n3\\n3 I 3\\n\u00e2\u0096\u00a0D-\\nN\\n1\\nP\\n3\\nt\\nCM\\n3\\no\\nCD\\nJ-\\n3\\n3\\nK\\nr-\\n3\\nK\\n3\\nCO\\noo n\\n3\\ny\\nCM\\nCO\\n00\\n3 Y~\\nY Y\\nCO CO\\nto\\nCM\\nco\\n02 2\\nY Co\\nCM\\nCO\\nco K 00 CO\\nco N co\\n02\\n3\\n1^\\nCD\\nO\\nCM\\nv\u00e2\u0080\u0094\\n3 O\\nCM\\nT _\\n3\\n3\\n3\\nCM\\nt- 3\\n(J)\\n(J)\\n3\\n3\\nLO\\nN.\\nCO\\nCO\\nco CM\\nY 3\\nCM\\nco\\nCD 02 CO CO CO\\nr- 02\\n(O O K\\nCO 3 CO co\\nD- 3\\n3\\n3\\nK\\n3\\n3\\n3\\no\\nh- C\\\\4\\nCO\\nr- 00\\nCO CD CO\\n3\\n3\\nO\\n3\\n3\\n3\\n3\\nr- N\\nG\\nCO\\nI s\\n\u00e2\u0096\u00a0M-\\n3\\n00\\n3\\n3\\nK\\nCO\\nT\\n3\\nY\u00e2\u0080\u0094\\n3\\n3\\no\\n3 \u00e2\u0096\u00a0Y\\nO\\n(O 3 3\\nD-\\nO\\nO)\\n3\\n3\\n3\\nT- 3\\n3\\n3 D\\n\u00e2\u0096\u00a0Y\\n3\\n00\\nY-\\n3\\nT\u00e2\u0080\u0094\\nK\\nr\u00e2\u0080\u0094\\n3 t-\\nY\u00e2\u0080\u0094\\nLO JO\\nY UJ\\nCM\\nco\\nO\u00c2\u00a9C000\u00c2\u00a90 )OO\u00c2\u00a9C0 (MM l fl t(DN\\n0^\u00c2\u00a9(OpNlOO)O^M--lncON\\nCO N N lo ID T- K -r- CO\\nN \u00c2\u00ab2 lO C0\\nf- Y 3\\nCM\\nco 00\\nCM\\nCD N CD CO CO\\nr- Y CM\\nCD 3\\nY JO\\nco\\nY33K3|^.K00333O2 t --33\\n-r-LD33Y3C03YY3 CO -r- CM\\n020 K 02 3 ID t\u00e2\u0080\u0094 CO CM M\\nJ- CD\\nO CO\\nco jo\\no\\nco\\no\\nY\\nCO CO\\nY\\n00 CM N M\\n3\\n3\\n3\\nK.\\n3\\n3\\nCM\\nCD Y\\n3\\nY\\nS\\n3\\n3\\n3\\nY\\nCO\\n3\\n3\\n1^.\\n3\\n5\\n3\\nY\u00e2\u0080\u0094\\n3\\n3\\n3\\nCM\\nK t- CO\\nCO OJ M\\n02 CM CD CO CO\\nCO ID CO\\n3 Y Y 3 3\\nCO CO CM\\nD- K\\nCO\\nco\\n(Dl0\u00c2\u00a90)C0(D2t00^On(DOCMWW\\nLD02CmK1DO t ~O 00CDC0 CO r^- CD\\n00 CO co CO CO f CO CO T- CM\\nN ID K O\\nN co CO\\nT- N N\\nt- CD CO CM\\nt- o N. CO 3\\nT- 00 CO co T-\\nLO\\no\\n3\\n3\\n3\\nCM\\nY\\n3\\nO\\n3\\nCO\\nN\\n3\\n3\\n3\\n3\\n2\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\u00e2\u0080\u00a2\\nO\\n|Y\\n3\\n|Y\\na\\nCO\\n3\\nCM\\n3\\nD-\\nCO\\n3\\nO\\nCO\\nK\\n3\\n3\\n3\\nO\\nO\\nCO\\n3\\nY\\n3\\n3\\n3\\n3\\ntY\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nco\\n3\\n3\\nN\\n3\\n3\\nCD\\nCM\\n3\\nY-\u00e2\u0080\u0094\\nO)\\n3\\n3\\nO\\n3.\\n3\\nCD\\n3\\nT-\\n5\\n3\\n3\\nco\\n3\\nY*\u00e2\u0080\u0094\\n3\\nto\\n3\\nT-\\nT\u00e2\u0080\u0094\\n3\\n3\\ny\\nY\u00e2\u0080\u0094\\n3\\nT-T\\nY\u00e2\u0080\u0094\u00e2\u0080\u00a2\\nY-.\\no\\n3\\nCO\\ny;\\ny;\\nID\\ny:\\ny:\\nI s\\n3\\n3\\nY\\nY\\nCD\\nT-*\\no\\n3\\nO\\nY\u00e2\u0080\u0094\\n0\\n3\\nK\\n3\\nY\u00e2\u0080\u0094\\nCO\\nO)\\n3\\nY\\nr-\\n0\\n2\\no\\nCO\\nS\\nz\\n3\\n3\\nCM\\nLO\\n3\\nO\\n3\\nY\\nY\u00e2\u0080\u0094\\nCD\\nO\\n3\\n3\\nCM\\nY-.\\n3\\n3\\n3\\nz\\nK\\n3\\n3\\nz\\n3\\nID\\nT\u00e2\u0080\u0094\\nY\\nY\u00e2\u0080\u0094\\nNT\\n3\\nY\u00e2\u0080\u0094\\n3\\nY\u00e2\u0080\u0094\\n1\\nt-T\\nLO\\n3\\n3\\nY\u00e2\u0080\u0094\\n3\\n0\\n3\\n3\\nO\\nO\\nK.\\n3\\nY\\nY\\n3\\nY\\nY\u00e2\u0080\u0094\u00e2\u0080\u00a2\\n3\\n3\\nCM\\n|Y\\nCO\\nD-\\nO\\n3\\nco\\nr-\\n3\\n3\\n3\\nO\\n3\\n-T\u00e2\u0080\u0094\\n3\\nY\\n\u00e2\u0096\u00a07\\nr-\\n3\\n3\\nK\\n3\\nY\\nK\\n3\\n3\\nz\\nco\\nY\\nCO\\n3\\n3\\nK\\nY\u00e2\u0080\u0094\u00e2\u0080\u00a2\\nj\\n3\\nl\u00e2\u0080\u0094\\nO\\n3_\\nLD\\nY^\\n3\\n0\u00c2\u00b0.\\n3_\\n3\\nT\u00e2\u0080\u0094\\n1\\n3\\nY\u00e2\u0080\u0094\u00e2\u0080\u00a2\\n3\\n0\\nt\u00e2\u0080\u0094\\nCO\\n3\\nY\\nr-\\n3\\nCD\\no\\n3\\n1\\ny~~\\n\u00e2\u0096\u00a0r-*\\n3\\nT-\u00e2\u0080\u0099\u00e2\u0080\u0099\\n1\\nT-\\ny-T\\nT\u00e2\u0080\u0094\\no\\n3\\n3\\nY\\n3\\n3\\nCO\\n3\\nO\\n3\\n3\\nT-*\\n3\\n3\\nY\\n3\\n3\\n3\\nIP\\nO\\nO\\nO\\n3\\nCO\\n3\\n3\\n3\\n3\\nO\\n3\\n3\\nK\\nO\\na\\nK\\n3\\n7\\n3\\n3\\nK\\n3\\n3\\n3\\nJD\\n3\\nY\\n|Y\\n2\\no\\nO\\nCO\\n2\\n3\\nY\u00e2\u0080\u0094\\n3\\nCM\\no\\n3\\n3\\nK\\n3\\nLO\\n3\\n3\\n1\\n3\\n3\\n3_\\n3\\nY 1\\nT\u00e2\u0080\u0094\\nCO\\nY\\n3\\n3\\nNT\\n3\\n3\\ny\\ni-J*\\nT-\u00e2\u0080\u009d\\nT-*\\ny\\nCO\\n3\\nT-\\np\\ncj\\nUJ\\n\u00e2\u0080\u00a2\u00e2\u0080\u0094J\\nUJ\\n00\\n5\\nO\\nO\\nUJ\\ng\\n02\\n2\\n.02\\nC/2\\n3\\no\\nc\\nE\\nD\\nCD\\n3\\nO\\na\\nI o\\n-J\\n3\\no\\nO CO\\nQ\\n5\\nCD\\nO\\no\\n-Q\\n\u00e2\u0096\u00a0O\\n3\\nCD\\nC\\nCD\\n02\\nCD\\n\u00e2\u0096\u00a0g i\\n5 1\\nCD\\nD\\nJO\\no\\nO\\ncO\\nc\\nQQ\\nCD\\n3\\nO\\nc\\nE\\n3\\nCD\\nCD\\no\\nt o s\\n02\\nUl\\ng\\nCD\\nO\\nO\\nCD\\n3\\nO\\nc\\n3\\n5\\n-Q\\n3\\nCD\\n02\\n2\\n.02\\n*s\\n02\\nG\\n03\\n02\\n\u00e2\u0096\u00a0C\\nCD\\nC(2 .CD\\n8 6\\n02\\nO\\nc\\no\\n02\\n3\\nJD\\no\\no\\nro\\nQ2 E\\n-C Q2\\n4\u00e2\u0080\u0094 1\\nO\\nCQ\\n5\\no\\no\\n03\\nCO\\nO\\n03\\nO\\nO\\nO\\n15\\n15\\n15\\nc\\nc\\nc\\n0\\n0\\n0\\nD\\nD\\nCJ)\\nCO\\n00\\nc\\nc\\nc\\nro\\n03\\n03\\n0\\n*o\\nO\\n02\\nCD\\n0\\nE\\nE\\n0\\n0\\n0\\nO\\n0\\nO\\nro\\nc\\n02\\n\u00e2\u0096\u00a0g\\nCD\\n02\\n0 c\\nQ.\\n02\\nO\\nX\\nUJ\\n-Q\\no\\nCD\\n3\\nO\\nc\\nE\\n3\\nO\\nn\\n\u00e2\u0096\u00a00\\n0\\n2_\\n0\\n-Q\\n0\\n_C\\nO\\nO\\nC/2\\n3\\n02\\nO\\nc\\nC\\n0\\nc\\n02\\nE\\n3\\n0\\n;g\\nT2\\n.to\\nC/2\\n*6\\n-S\\nO\\n0\\nQ2\\nQC\\nCC\\nAppendix A National Emissions (1970 to 1998) A-19", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0219.jp2"}, "220": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nT3\\nD\\n3\\nC\\n\u00e2\u0080\u00a24-J\\nc\\no\\nYt\\nI\\n0)\\nJD\\nco\\nH\\no\\noj|\\n0J\\n4-*\\nCO\\no\\nQ\\nO\\n3\\no\\no) o m t\\\\i\\nT- O\\nCM CM CM\\n0 Tf 00 o c\\\\l\\nJj o o\\nCM CM CM\\n-M- CM CM\\n03 O o\\nCM CM CM\\noocM^coOiOM-cocnh- L C)cD l -OT---^cococop^rocooco x)r^oooco\\nco foo ~co co i- f ro O) rt if) co k o M in co t-\\nYJ- CM Y t- f i CM CO r-CMf-\\nYJ- CM\\nCO\\nCO\\nCO\\nCM\\n03\\nCO\\n00 [O Tt\\n0 CO 0\\ny\u00e2\u0080\u0094\\n10\\n1^- 0 0 0 CO\\nJ)\\n03\\nCO\\n00\\nco\\n0\\nCO\\n00 T-\\n00\\nCM\\nT\u00e2\u0080\u0094\\nCO\\nT\u00e2\u0080\u0094\\nCM\\nT\u00e2\u0080\u0094\\nCO CM 00\\nYt CM\\nCO\\nCM\\nK\\nuf)\\nIf}\\n1\\nCO\\n03 O M\\nO CM\\nO O\\nCO\\n03\\n03\\nCO\\nco CO\\nco\\nO\\nCO\\nCO\\nCM\\nCO\\nT~\\nCM\\nCO M CO\\notoo)io o-oinooM-0 -NiocoiOT-eoO)0)2\\nCO O) Cl) 1 CO (O K C\\\\| in in 1 IO CO CO\\nCM i\u00e2\u0080\u0094 IT) CO t\u00e2\u0080\u0094 CO\\nT-cowonnoMocM\u00e2\u0080\u0099-\\nN QO CQ o T- CO N\\nCM YJ- 1 CM i\u00e2\u0080\u0094\\n03 M-\\nT- Tt 0 O 00\\nCM\\ny\u00e2\u0080\u0094\\nCO\\nCO\\nCO CO\\n03 03\\nm\\nco\\ncm cn\\n00\\n00\\nCO CO CO\\nO 03\\nO CM\\n00\\nCD\\nco\\n03\\nO\\nCM CO\\nm\\nt- K\\n03\\n03\\nr-\\n00\\n00\\n03\\nO\\nCO\\nlo\\nCO\\nCM\\nY\u00e2\u0080\u0094\u00c2\u00bb\\nco\\nCM\\nY\u00e2\u0080\u0094\u00c2\u00ab\\nCO\\nT-\\nCM\\nCO\\nCM\\nk j\\nco tj- cm\\nco\\nCO\\nCO\\nCM CO\\nCO\\nh- CM CO\\nO CO\\nO CM\\nO\\nCM O O\\nCO\\nco\\n03\\n03\\nI\\n00\\n03\\n03\\nT\u00e2\u0080\u0094\\n1\\n1\\nO\\nco\\nCM\\nY-\u00c2\u00bb\\nCO\\nCM\\nT\u00e2\u0080\u009c\\n1\\nCOO)COO) M-T- M OO l 00oKt-lOIOcOCOCOCOCMCMin!00|v.CpoOOa)OOCOCM\\nK o 03 F CO CO YJ- CO lfj in T- O) O) t\u00e2\u0080\u0094 CO CO 03 T- h~ CD O\\nC\\\\| c\\\\| T\u00e2\u0080\u0094 CO CM i\u00e2\u0080\u0094 O- 00 T ~CO t\u00e2\u0080\u0094 CM i\u00e2\u0080\u0094 i\u00e2\u0080\u0094\\n005COCOCO^-5t oi^-CMlO M-CO\u00e2\u0080\u0099~COOOCOCOcOCpCMrfCMCMtv.CpcOOCOOr^tOCMOO\\nco oo F m to o cj o m oj oj co 03 a cm cdcoo\\nCM CM CM T* CM T- Co CM T CO t- CM t-\\nco\\nCO\\nN O rf\\ncn t- t- r~\\nCM CM CM\\nCM\\nCO CM\\nm co\\nCM CM co\\n0\\nCM\\nCJ\\nCM r}-\\nCO\\nY\u00e2\u0080\u0094\\nTf 03 CO\\nO CD\\n0 in\\ny\u00e2\u0080\u0094\\n0-00\\nm\\nCO\\nCM\\nCM\\nO\\nCO\\nCM\\n03\\nCO\\n03\\nY\u00e2\u0080\u0094-\\nCO\\nY~~\\nCO\\nCM\\nY\u00e2\u0080\u0094\\nCO CM\\nCO CO\\nin\\nCO\\nK\\nCO\\n0\\ncn in\\nos\\nCO\\nco\\nt~ CM\\nJO\\nK\\nr- C\u00c2\u00a33 CO\\nO CO t-\\ny-\\nCM\\nP 5\\nCM\\nCO\\nCD\\n1 CM\\nin\\nco\\n03\\nN.\\nCJ\\nCO\\nCD\\nK.\\nco\\nin\\nCO\\nY-*\u00c2\u00bb\\nY\u00e2\u0080\u0094\\n\u00e2\u0096\u00a0o-\\nCM\\nY^.\\nYJ-\\nCM\\nY\u00e2\u0080\u0094\\no o\\n03\\n03 r-\\n2 CD N Tf O\\nCO\\nK\\n03\\nco\\nco\\n03\\nn- CM\\nCD CO\\n03\\nK\\nr~ CO\\nYf\\n1 -M-\\nCO 7\\nCM\\nY\\nY~~\\nCO\\nCD\\n1 YJ-\\nin\\nco\\n00\\nCO\\nCO\\nK\\nin\\nco\\nY^\\nY\u00e2\u0080\u0094\\nYJ-\\nT\\nCM\\nto o m\\nCO\\nCO\\nco r r~ o o\\nCO N O)\\nCM\\nIO\u00c2\u00aeTt(OOOSTj 0 (DCMcO l O C\\\\| fCMCOi tJ\\\\iCMo(M5 r-tf)COO -T-(00 |WoO\\nCO-^un M- F N^in OCM 0* Ni-OoO O^oo CM CO 00 03 03\\nYJ- COCO CO co co in CM c\\\\| COCM YJ- 1 CM\\nF\\nCMO) 03 -!\u00c2\u00a3?r CM 3 NK^:i^oK eo co T}-OM-\\nMNC0C0O)Kc07C )in l n NC0M9 -97CM7O)C0IO79\\nCO CM C) in^^T-^^LnCOCM^Ol^-^-CM^CDCO\\nco\\nCO\\nCO\\n0 T-v~^r oCMC303-!0\\nl7N N ?7777-\u00e2\u0080\u009c rr\\\\ rv\\\\ r*.\\nin\\nK\\n00\\nco\\no-\\nCO\\n\u00e2\u0080\u00947\\nin\\nQ\\n03\\nCO\\nco\\nco\\nC0 9 eft\\ncm cm\\nj)in oswcoM ^coiO rM 0 o 0 co r- 0\\n3(DJ(OKf 0O7^NK in^Cp7jt 77 (O7N^(O77\\nepv ns fA K. lq CO C\\\\j N lq If)\\nCO\\nT ir co w\\ny* Tt co\\nK\\nK\\n0\\nCO\\nin\\nr-\\nO\\nO\\nO\\nCO\\n0\\nCO\\nco\u00e2\u0080\u0098\\nK\\nco\\n03\\nCO\\nT\u00e2\u0080\u009c\\nz\\nco\\nCO\\nY\u00e2\u0080\u009c\\nY\u00e2\u0080\u009c Y^\\nh~\\n00\\nM-\\n03\\nCM\\nz\\ni\\nCO\\nI s r~\\nCD CO\\nco\\nI\\nF\\nCJ\\n:j\\nQ\\no\\nDC\\na.\\nQ TS |j\\noj\\n03\\nO)\\ncn\\niy in 8\\n-J .co p\\n5 E\\n\u00e2\u0080\u00a28 fk\\no\\nc\\nCO\\n03\\nO 5 03\\nQ\\n3\\no\\ng\\nc\\nCO 03\\n2 o\\nly o\\nX\\no\\n3\\no\\nI\\no\\n0\\nc\\ncn\\n03\\nDC\\nE\\n03\\nJO\\no\\n\u00c2\u00b03 2 fc\\n5 s\\n3\\n03\\nE\\nCO\\nc\\nLU\\nC\\n03\\n3\\ncr\\no\\nCO\\n03 2=\\nII\\nO O)\\n0.\\n03\\nc\\ncn\\ncn\\n03\\no\\nO 2\\n03 03 2 CL\\nI I 55 2\\n(0 5\\nto co In C13\\nc I S 2\\nO 0\\no n: ct\\nco o\\nE 0\\nJ= 03 .j\\nsz g\\nb\\n03\\n8-2\\nC3\\nE\\n3\\nc\\nE 03\\n5\\nCO o\\n03\\nc\\nc/3 O\\n5 LU\\no\\no\\nk_\\nCL\\n_co\\n03\\n4\u00e2\u0080\u0094\u00c2\u00bb\\n03\\nUj\\n5\\n:3\\nQ\\nQ\\nUj\\nDC\\n03\\n,c\\ncn\\nw\\n03 0{J\\no\\no\\nL_\\nCL\\n03\\n4\u00e2\u0080\u0094*\\n03\\nc\\no\\n0\\n3\\n\u00e2\u0080\u00a2O\\no\\n1\\nCL\\ncn\\nCO\\no\\noS\\nw\\ns\\nO)\\n5\\n3\\ncn\\ng\\nl.\\ncn\\n3\\n\u00e2\u0096\u00a0O\\nc\\n\u00e2\u0096\u00a0O\\n03\\n_cg\\n03\\nDC\\n08\\ncn\\ng\\nu\\n03\\n55\\nDC\\nE\\nI\\n5^0\\nc o\\nM3\\nc\\n3\\nO)\\nc\\n-5\\nu\\n8\\nCJ\\n0\\ns\\n\u00e2\u0080\u00a22\\nCO\\no\\nT3\\n3\\n03\\no\\n03\\nCL\\nP 5\\nUj\\nCO\\nco\\nUj\\no\\no\\n03 DC\\nc 0.\\n3\\nE\\nI\\ns\\nE\\no\\nCJ\\n3\\n\u00e2\u0096\u00a0O\\no\\n5\\ng cd\\n\u00e2\u0096\u00a0O\\nc\\nk\\n08\\no\\n2\\n3\\nc\\nco\\nco\\n-C\\nGl\\ncn\\nCO\\na.\\nO.\\n08\\n\u00e2\u0096\u00a0D\\n8 l\\nco\\ncd\\nk_ _l\\n3\\n\u00c2\u00b11 CO\\n3 a)\\nO\\n03\\nF\\nCO\\n8 2\\n\u00e2\u0096\u00a0O o\\nO 3\\n2\\n03\\n.cn w\\nJD 2\\n3 CL\\n0 cn\\nQ- 03\\n03\\n\u00c2\u00a3T\\n08 g\\n2-\\nCL\\nT3\\no 0\\nO _Q\\n3\\nDC\\no\\ng\\n3\\n\u00e2\u0096\u00a0O\\no\\nCO\\nL_\\n03\\nc\\n0\\nt\\nE\\nc/)\\n4-4\\nc\\n9\\nCD\\n\u00e2\u0080\u0098d\\nO\\nE\\nCT\\n2\\nZ3\\nO\\nO\\nQ.\\n\u00e2\u0080\u00983\\nUJ\\nc\\nE\\nL_\\nCL\\nCT\\nLU\\n0\\nc\\nCD\\n2\\nCD\\ng\\nc\\nc5\\ntl\\n0\\nE\\nCD\\nQ)\\n2\\nC\\njc\\n0\\nt_\\nQ_\\n1\\nCJ\\n0\\n0\\n0\\nc\\n03\\nCD\\n03\\nLU\\nL_\\nF\\ncn\\n03\\ncn\\ncn\\nCD\\no\\no\\nt\u00e2\u0080\u0094\\nCL\\ncn\\n3\\no\\n03\\nc\\n2\\n03\\no\\nA-20 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0220.jp2"}, "221": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n~o\\n0\\n3\\nC\\nMM\\nc\\no\\nI\\nQ)\\nn\\nco\\nI-\\nOO ^OOOOOCOoOOOOOOOCMCviO O^T-Ov-oOO-r-OOoJpoOOCTilO^-r-in\\nCO CM\u00e2\u0080\u0099\u00e2\u0080\u0094 CM CO CO CD D CO f- CO\\no\\n0\\nco\\no\\no\\no\\nw\\n3\\no\\nC/5\\nOOOOOC\u00e2\u0080\u0099JOOOOOOOOCMCMCnCOC\u00e2\u0080\u0099O\\nCM M\\nOOOOOCOOOOOOOOOC\\\\J\u00c2\u00bb~CT)COOO\\nt CM CM\\nOOOOOCMOOOOOOOO\\nOOOOOCMOOOOOOOO\\nK W CO N\\nco CM\\nO CM N. co\\n0 M- CM\\nO\\nCO\\nO OOT-OOoC\\\\|COKOh.M-M-^in\\nCM CM CM O) co co 1 CO\\nCO T\u00e2\u0080\u0094\\nO OO\u00e2\u0080\u0099-OQoCOh-KOuoCMCOT-cO\\nCM M OlCOCO\u00e2\u0080\u0099-OO\\nOr\\no oooooo3 \u00e2\u0080\u0099cd t-o\\nS^ZZ^ZZ^\u00c2\u00ae\\nO OOOOOC0J~t- O CMCD\\no^zz^zz-^\\n\u00c2\u00bb~oo ooioooo oooo-M- \u00e2\u0080\u0099-ipcp\u00e2\u0080\u0099- 0 \u00e2\u0080\u0099~oooooocoKr^ o \u00e2\u0080\u0099-CT)\\nZ 2 n in cm c\\\\i r- T\\nto T\u00e2\u0080\u0094 c\\\\l\\n*-oooooo lT -oo oooor-2;cMcoK^o oooooo T -coco CT. oco\\n2 co CM K^ 2 Z^ZZ-co\\nC)OO OOQ\u00e2\u0080\u0099-NO OOOO\u00e2\u0080\u0099- 2 ;CMM-C 0 ^OOoOOOOO\u00e2\u0080\u0099-C C 0 a)\\nCO CM T- N -M- -5 ID -7\\nCs, rf\\nco\\no co\\nm\\nCO\\nooo ooN-OLOo oooO\u00e2\u0080\u0099-cMcMcocoT-oooooooooCMco fr~ a r\u00e2\u0080\u0099-r^\\nz z ^COCM-- S 2 zz^zz-cc\\no o\\nO CO O t- T-\\n00 T-0\u00e2\u0080\u00980 0\\nooc\\\\icocoocoooQK r oooo\u00c2\u00aein nCicociO\u00e2\u0080\u0099~-\\n2 CO CM ZZZ h\u00e2\u0080\u0099M-M- lO CO CM\\nlo T-\\nOOCMCOCO\u00e2\u0080\u0099-KooQCO oOOoCOtJ-M-OcoK\u00e2\u0080\u0099~-\\n2 co cm ZZZ jo \u00e2\u0096\u00a0o- o- in co cm\\n2\\no\\np\\n-1\\np\\n3\\nK\\ns\\nC/)\\no) r\\ncd .y\\nS\u00e2\u0080\u0099\\nQ O\\no\\no\\no\\no\\n0\\no\\nn3\\n\u00e2\u0080\u00a2c\\n3\\nc/d\\nK\\nQC\\no\\nI\\n1\\nOfl\\nUJ\\n3\\n2\\ne\\nco\\nc\\n0\\nCL\\nOS\\nn\\n0\\nc\\nE\\n|2\\n3\\nCQ\\n\u00e2\u0096\u00a0c\\n0 o\\nO) Q-\\n0 2\\ni\u00e2\u0080\u0094 c\\no 0\\nCO H\\no o\\n3 3\\nT2 TD\\no o\\nU k_\\nCL CL\\nE E\\n3 3\\na) 0\\no o\\nk_ i_\\n0 0\\nCL CL\\nofi ofl\\nE E\\n3 3\\n_0 0\\no o\\nk_\\n0 0\\n0. CL\\ntr\\nCD\\nr\\no\\nCD\\no\\nO)\\nQ.\\n05\\nQ-\\nCD\\nCD\\nL_\\nW\\nC\\nk_\\nO\\nC\\nCD\\no\\nCD\\nk_\\nCO\\nH\\nCO\\ni-\\n_\\nCD\\n*CD\\n0\\nCD\\n0\\nco\\n..00\\nwoo\\no E E\\n*=0 0\\n0 JC -C\\nco o o\\n0 Q o\\no\\nt\\n0\\nco O O\\no o\\nE E\\no\\n-J\\na\\no\\n0 UJ\\nCO QC\\n0\\no 2\\nco\\nCO\\n0\\no\\no\\no\\no\\nc c\\n0 0\\nCO CD\\n0) 0 o (0\\n-C JC 0 O\\nO O -C v\\no o 5 J\\nc c\\n0 0 S\\nO uj\\nk_ L_ -Jt\\n003\\nCD\\n0.\\n0\\nQ\\nCO\\ni\\n.0\\nc\\no __\\n\u00e2\u0096\u00a0ffl 5\\n0 O\\nc .c\\no\\nc\\nCO\\nc\\n\u00e2\u0080\u0099c\\nL_\\n0 m\\nc\\nO 0\\nQ.\\no\\n0\\nI\\nc\\nV.\\n0 _\\n5\\no t-\\no\\nCL\\n0\\n0\\n0\\nto\\n0\\n0\\nCO u_\\nQ\\nCO\\nL I_\\n.0\\n_w 0\\ns -s\\n\u00e2\u0096\u00a0O c\\nc\\n0\\n0\\nJC\\no\\n0\\n-C\\no\\nyo\\nUJ\\no\\nI\\nQ\\no\\nQC\\nCl\\n0/5\\nCO\\n0\\ng\\nsz\\n0\\nV)\\n0\\nu\\n3\\n9 s\\n\u00c2\u00abL O)\\nO)\\n0\\n0\\n,o\\ns\\n2\\n0\\n0 W\\nCO 0\\n5\\n73 s\\n*L o\\nO) I\\n(M\\nc n\\n0\\n0)\\no\\no\\no\\n!c\\no\\n3\\ni-\\n5\\n2\\nH\\n0\\n0\\nc n\\nC/)\\n0\\n0\\nCD\\nCD\\nCo\\nCO\\nO\\nO\\n3\\n\u00e2\u0096\u00a0O\\n\u00e2\u0096\u00a0S\\n1\\n3\\nQ\\nq\\nd:\\n.Co\\n-c\\n.O)\\nCO\\nCD\\nID\\nCO\\no\\nCO\\n*~oo t-o J- ot- ooi- 3 ino l ooDO\u00c2\u00b0o oc OoCMco l ooin oo\\n2 Z ZZ CO CM ZZZ fN M t uoCO\u00e2\u0080\u0099\u00e2\u0080\u0094\u00e2\u0080\u0099\u00e2\u0080\u0094 t\u00e2\u0080\u0094\\n\u00e2\u0096\u00a0L lo T~ T- CO\\nS S 5r;3r;\u00c2\u00ab5^ 55 j;(;cooocoiooco\\n5zzzzz2zzzzzzzzz CocvJ S Cvj r -Z ~z zzzSSz^!^!^ mco\u00e2\u0080\u0099-^-o\\nt i90 ^S 5 f v K S!5oo Q o C 3 oo c c oa co\\ng^zzzzSzzzzzzzzz^^S^^S^z 2 zzS2z^^12 tj- co oo\\n^ZZZZZ^ZZZZZZZZZ 5 Z ZZZZZZZp ^$2 \u00e2\u0080\u0099t CM CO\\nCO\\n0\\n0\\nX\\n_W\\n0\\nW\\n0\\nAppendix A National Emissions (1970 to 1998) A-21", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0221.jp2"}, "222": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n~o\\nD\\n3\\nC\\nc\\no\\nrr\\nl\\nQ)\\n(0\\nh-\\nC5\\nCO\\nIT)\\nCM\\nCO\\no\\nIT)\\nO\\nCN\\nCD\\n05\\nin\\nCM\\nID\\nT\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094\\n7\u00e2\u0080\u0094\\nCNJ\\n05\\no\\nCO\\nCM\\nCO\\no\\nt-T\\nctT\\nE\\n0\\nsz\\nCD\\nCO\\nCO\\ny\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\nCM\\nN.\\no\\nr^\\nO\\n7\u00e2\u0080\u0094\\n05\\nr\u00c2\u00bb\\nCM\\nCO\\n1\\nCO\\ny\\nT-\\ni\u00e2\u0080\u0094\\nCsl\\n_c\\n05\\nT\u00e2\u0080\u0094\\n3\\nT-\\nCO\\nCM\\nof\\n\u00e2\u0096\u00a0O\\n0\\n7\u00e2\u0080\u0094\\nc\\n*0\\nID\\n05\\nCO\\no\\nT\u00e2\u0080\u0094\\n05\\nCO\\nCM\\no\\no\\no\\n7\u00e2\u0080\u0094\\nC\\n05\\n05\\nCM\\n1-\\nCO\\ny\u00e2\u0080\u0094\\nr\u00c2\u00ab-\\n2\\nT\u00e2\u0080\u0094\\n00\\no\\n05\\n05\\n5\\nCM\\nT\\nr-\\no\\nof\\n0\\n-r-\\n0\\n\u00e2\u0096\u00a0O\\n3\\nCO\\no\\nT\u00e2\u0080\u0094\\nCM\\nCO\\nCM\\nio\\nin\\no\\no\\n3\\n05\\n05\\nCM\\n05\\nT\u00e2\u0080\u0094\\nID\\nT\u00e2\u0080\u0094\\nV*-\\n2\\n7\u00e2\u0080\u0094\\nr-\\n-Q\\n05\\n05\\nID\\nCM\\nT_\\n00\\n0\\nCM\\n0\\nCO\\nCO\\nO\\n05\\nCM\\nO\\nG)\\nT-\\nCO\\n\u00e2\u0096\u00a0o\\n0\\n05\\nIM\\nCM\\nT\u00e2\u0080\u0094\\n\u00e2\u0096\u00a0M-\\nT\u00e2\u0080\u0094\\n2\\nCO\\n05\\n05\\nLO\\nCM\\n0\\nc\\\\T\\n0\\nCM\\n\u00e2\u0096\u00a0D\\n0\\nCM\\nCO\\nCM\\n05\\ny\u00e2\u0080\u0094\\nCO\\nD\\nCM\\no\\nCD\\no\\nCO\\nO\\n05\\nco\\nCM\\n\u00e2\u0096\u00a0st\\nT\\nD\\nCM\\nY\u00e2\u0080\u0094\\n2\\no\\nF\\n05\\n05\\nID\\nCM\\ni\u00e2\u0080\u0094\\n00\\nL-\\nCN\\n0\\nCM\\n-C\\n0\\n0\\n_\\nCM\\n05\\nT\\n05\\nO\\nCM\\nT-\\no\\n7\u00e2\u0080\u0094\\n05\\nCM\\nCM\\ny\u00e2\u0080\u0094\\nID\\nCM\\nY*\u00c2\u00bb\\n2\\ny\\n05\\n05\\nID\\nCM\\nT\u00e2\u0080\u0094\\no\\n-Q\\ni\u00e2\u0080\u0094\\nco\\nJ0\\nCM\\n\u00e2\u0080\u00990\\no\\nCO\\nCM\\n05\\ny-\\nCM\\nCM\\nC\\\\J\\nC\\\\J\\no\\nO\\n0\\n05\\nY\u00e2\u0080\u0094\\nCM\\nO\\nT\u00e2\u0080\u009c\\nD\\nCM\\nY\\n2\\n7\u00e2\u0080\u0094\\nCO\\nO\\n05\\n05\\nID\\nCM\\nt\\nCO\\nC\\nT\\nco\\n0\\nCM\\nk_\\n0\\n05\\n05\\nCM\\noo\\nh-\\nCO\\nCM\\nY\u00e2\u0080\u0094\\nT-\\nCO\\nLO\\nCO\\nCD\\n00\\n05\\nK\\nN\\nCM\\nCO\\nt\\n05\\nco\\nY\\nZ\\nz\\n(J)\\nCM\\nS co t-\\n2 W N\\nQ CO\\nCD\\nCM\\nTf CO CM O CM O\\nt CO N\\nCM CO\\nK\\nt- m cm\\nCO CO N -7\\nr--\\nCM\\nN o r-~ co co o t-\\nco cm o -m- in\\nCO t\u00e2\u0080\u0094\\ne\\nip coh CO r;\\nz z\\nLO\\n0 xfCMCO 0 0\\n05 -7 77 ID 7 t\\\\| 7 CM 7\\ncn M-cnco o o\\nco 7 7 n 2\\nz z\\ncu\\nm\\no\\nS\\nQ\\nS\\nfO CD\\nUj c\\no 5\\no b\\nX3 O\\nCD CD\\nO O\\n2\\nlu\\nQ\\no DC CE\\n(t c\\n-i\\n2\\nz\\n0\\nk_\\no\\n_C0\\n0\\n0\\n\u00e2\u0080\u009c6\\n9 8\\ncn\\nCD\\nDC\\nffl SQ\\n.c 3\\ncJ uj\\n\u00e2\u0096\u00a0o 2\\n3\\nH\\no\\n2\\nCO\\nCD\\nh_\\no\\nu_\\noS\\nD\\n3\\no\\n\u00e2\u0080\u0099Em\\nCD\\nc\\no\\nw\\n3\\nJD\\nE\\no\\nO\\nk.\\n0\\n_C\\nO u.\\n\u00e2\u0096\u00a0C\\nI\\n05\\nc\\n\u00e2\u0080\u0099c\\nc\\no\\nCD\\n-Q\\nk_\\no\\no\\nk_\\no\\nQ_\\nk_\\n0\\n_C\\n\u00e2\u0080\u00990\\nC\\no\\n0\\nE\\n0\\nCO\\n0\\nk_\\no\\nO)\\n0\\n0\\no\\n0\\no\\nk_\\n3\\nO\\n0\\n75\\nk_\\n0\\n0\\n0\\no\\nLL\\n0\\nk_\\nO\\nO)\\n0\\n0\\no\\n0\\no\\nk_\\n3\\no\\n0\\no\\no\\n0\\nQ.\\nn\\nTD\\n0\\n0\\no\\nO\\n75\\n0\\n2\\n3\\nO\\nO\\n0\\n0\\nn\\no\\nc\\np\\n3\\nO\\no\\n0\\n_C\\n0\\nCO\\nc\\no\\nCD\\no\\no\\nCO\\n05\\n05\\nCO\\nCM\\nO\\nk\u00e2\u0080\u0094\\nCD\\nX)\\nCD\\nCO\\nCD\\n05\\nCD\\nk_\\nLU\\nW\\nb\\nc\\no\\nco\\nb\\nc\\nCD r\\nCC T\\nig\\no CO\\nSI\\nQ.\\nb 2\\nN ro\\nO \u00c2\u00a7.CM\\nco _ i\\nm\\ncd c r_\\nco o\\nCD :p\\nCO o co\\n_ 05 0)\\nra CO 3\\nCD C 7c\\no\\nCD o D\\nO 3\\nC O\\n5 O -g\\nCO\\nO CD CD\\nX\\nC\\n05_\\n2 o O.\\nO Oic\\nCP \u00e2\u0096\u00a0O 3\\nzl E\\nD 2 wT\\n-c E c\\nb m o\\nO\\nCD\\nTO E\\nID C\\nCD O\\no\\n0 tS\\n10\\nE 0 CD b\\nCD _Q CD\\n05 C/5\\n0) 3\\nW CO 5 3\\nCO CO -is\\n.52 o\\nPOO\\n5\\ny -?5 o\\nO 05\\nc\\no 05\\nCO CD S\\nS5i E t\u00c2\u00bb\\nco o\\n.SSag\\nr 2 m E\\no w\\n8 2 o\\no\\nJD\\n_CD\\ncD\\nCD\\nO\\nC\\nCD\\nH- CO\\nC 3 CD\\nE CD _Q c CD\\n18 I\\nE o q_ o J2\\nS O 0 CD O\\nCO 05 CD O\\nCD 05 fflD0 O\\nq _3 CO CO 2\\n5m 0 0\\n^LZ-O\\nCD\\n05 V.\\nCD CD\\n055\\nCD\\nCD\\nD -C p\\nN h-\\n0\\nO\\nA-22 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0222.jp2"}, "223": {"fulltext": "National Air Pollutant Emission Trends 1900-1998\\nD\\nC\\no\\nV)\\nin\\n0\\n;i\\nc 5 r\\n3\\ns-\\n0\\nO\\nD 3\\n1\\nLU\\no\\n0\\nLO\\ni\\n0\\n0\\no\\noj\\nl\u00c2\u00bb\\na\\no\\n0)\\no\\ni_\\nZ3\\nO\\nw\\ns 1-co ^5^ C0C0\\nf) CO (o ffl (o Q\\nO) (D Ol lO C\\\\|\\ncm cm\\nKrj-lo p O) i/) IT) q\\n\u00c2\u00ab0 (O Ol K)\\nLM CM\\n?0 Y Y CO J- T 11) U) O\\nC K t\\\\| S\\nN CM\\n(O O) M M It)\\nt- y e^ y\\nCM\\n00 lo Y Y IX)\\nN M\\nCM\\nCO \u00c2\u00a3j O 03 IX)\\nt- O h- Y\\nCO\\nCp 00 P Ns\\nCM Y CO\\nM- (D CO CO\\nCM Y CO\\nco ro cm to\\nr Y Y\\nCO CO M\u00e2\u0080\u0099 roo!OOT-SOoC))IOT OMN 0\\nf\\\\ I \u00e2\u0080\u0094i \u00e2\u0080\u00944. nr\\\\\\nC\\\\J\\nJ \\\\U N VJ\\nN M CO CM S\\nCM CM\\nCJ) C0 CO COCM^O)CI)Ot-nNt- CO\\nN LO CO Y CM T- M) N If)\\nCM CM Cm\\nK -3- K CoCo^o.NQoCDCO tCOCO\\nLp CO CO Y CM 1- n N to\\nCM CM CM\\nN CM O) O) n M O O O\\nif)n ococM T-\\nCm CM\\nO) CO CO CO Y\\nCM CM\\nJ-COCO CT) Cm O CM o\\nk m O) cm cm y-\\nCM CM\\nCOt-COO)CmOt-OC)\\nK CD O) M CM 1\u00e2\u0080\u0094 t\u00e2\u0080\u0094\\nCM CM\\nLO Cp CM CO CO\\nt- Cp e- Y\\nCM\\ncm r co to\\nCM\\nY cp\\nCO in CO Co\\nY CO\\nK LO K CO\\nY CO\\nY CO\\nlO V\\nY CM\\nY CO\\nY CO\\nY CM\\nO CO CO o\\nM- CM\\nCO CM\\nY CO\\nCO CO O CJ)\\ny y\\nCM\\nco 2 o\\nY I s Y\\nCM\\nCOYOOCplOYYYp\\n-}CO -M- CM cm\\nCOYCOOOlOYinYC3\\ntj- co tj- CM cm\\nO 00 K io(OOcoCOOt-(OCl\\nCO CO CO Y\\nCM CM CM CM\\nCT) G) CO CM O O) 00\\nn o CO CO c\\nfo CM\\nin\\nCO CO\\nCM CM\\n\u00e2\u0080\u00a2*fr\\nJO\\nco\\nin\\n\u00e2\u0096\u00a0M-\\nC\\no\\nCO\\noo\\ny\u00e2\u0080\u0094\\nr^\\nCO\\ny\\ne\\ny\\nlo\\nY\\nco\\nK\\nT\u00e2\u0080\u0094\\nCO\\nCO\\n00\\nCD\\nCM\\noo\\nen\\nm\\nr-\\nCO\\ny\u00e2\u0080\u0094\\nY\\ny\u00e2\u0080\u0094\\nf\u00e2\u0080\u0094\\ne\\ni\u00e2\u0080\u0094\\nlo\\nY\\nr-\\np\\nr-\\nCO\\nCO\\nCM\\nin\\nY\u00e2\u0080\u009c\\n00\\nCM\\nCO\\np*\\nK\\np\\nT\u00e2\u0080\u0094\\ne~\\no\\nCO\\nin\\nco\\np\\nr\u00e2\u0080\u0094\\nLO\\n-M-\\n3\\nco\\nC\\\\J\\nCO\\n00\\nY\\nCO\\nCO\\nv\u00e2\u0080\u0094\\nr-\\nCO\\nCO\\nY\\nrj-\\n00\\nT\u00e2\u0080\u0094\\nCO\\nco\\np\\nm\\nCsJ\\nco\\nCO\\nh-\\nCO\\nCO\\nN.\\ny\u00e2\u0080\u0094\\nY\\nlo\\nY\\nco\\nT\u00e2\u0080\u0094\\nt\u00e2\u0080\u0094.\\nM-\\nCM\\nCO\\nin\\nCO\\nCM\\nY\\nco\\nK\\nF\u00c2\u00b0\\nT\u00e2\u0080\u0094\\ne-\\nCO\\nLO\\nY\\n-M-\\nK\\nr\u00e2\u0080\u0094\\nCO\\nT\u00e2\u0080\u0094\u00e2\u0080\u00a2\\n2\\nm\\nC\\\\J\\nco\\nCO\\nCO\\nCO\\nT\u00e2\u0080\u0094\\np\\nT\u00e2\u0080\u0094\\ni\u00e2\u0080\u0094\\nin\\nCo\\nm\\nCM\\nK\\nY~-\\nLO\\no\\nK\\n\u00c2\u00ab3-\\nCO\\nCO\\nin\\nCO\\n1\u00c2\u00b0\\nT\u00e2\u0080\u0094\\ni\u00e2\u0080\u0094\\nr-\\nco\\nCO\\nin\\nO\\nY*\u00e2\u0080\u0094\\nCO\\nCO\\nLO\\nCO\\nin\\nC3)\\ni\u00e2\u0080\u0094\\n00\\nCO\\nr 1\\no\\nCO\\nm\\noo\\n\u00e2\u0096\u00a0r~\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nCO\\nCO\\np\\nCO\\nCO\\nin\\nco\\ne-\\nN\\nCO\\ni\u00e2\u0080\u0094\\nCO\\nCO\\nO)\\nT\u00e2\u0080\u0094\\nY^.\\nCO\\nCO\\nrj\\nLO\\nin\\nco\\nr-\\nt^\\nK\\nCo\\nT\u00e2\u0080\u0094\\no\\nCO\\nco\\nin\\nK\\nY-\\nCO\\nCO\\n2\\nCO\\nC\\\\J\\nY\\nco\\no\\nh-\\nCO\\n3\\nin\\no\\nCT\\nT\u00e2\u0080\u0094\\nCO\\nlo\\nN.\\nCO\\no\\nY\\nCO\\nin\\nCO\\nin\\nCO\\n00\\nCO\\nz\\n5\\no-\\nCO\\nSi\\no\\nY\\ne\\n\u00e2\u0096\u00a0M\\ns\\nM-\\n2\\nO)\\nY\\nCO\\nz\\nen\\nY\\nN.\\no\\nK\\n6\\nLU\\nUJ\\ni\\no\\no\\nUJ\\nu.\\n0)\\nc\\nit) .O)\\n3\\nCO\\n3\\nO\\nc\\ni\\na\\n75\\no\\nO\\no\\nc\\nE\\n3\\nS\\n\u00e2\u0096\u00a0Q\\n3\\n0\\n\u00c2\u00b0a\\n0\\no\\n2\\nc\\nCO\\nL_\\nCl)\\n-c\\nCD\\nP\\nco\\nU\\n0)\\n-2\\n\u00e2\u0096\u00a0*3\\nco\\n\u00e2\u0096\u00a0Q\\n3\\nc PC\\nO ft\\ncp\\n=5\\n11\\no\\nO CQ\\n2 o\\nS3 O\\nO uj o\\nco\\na\\no\\nc\\ni\\n3\\n75\\no\\nCD\\nI\\no 5\\na\\ni G\\n\u00e2\u0080\u00a2t= 2\\n\u00e2\u0096\u00a0Q\\n\u00e2\u0080\u00a2Q 5=\\n3 C\\nCO CD\\n5\\nCD\\n-C\\no\\n0)\\n0\\nw\\nc.\\n8\\n0)\\nCD\\nL.\\nD\\n3\\nO\\n0)\\n0\\nTd\\ns\\n-3\\n\u00e2\u0080\u009c6\\nO\\nV) c\\nQ.\\no\\nCD\\n1\\ns .2\\nTo\\nCD\\nCO\\n3\\n.o\\nE O\\no\\nO OQ\\nco\\nCD\\nCD\\nJZ\\nllllg\\nci o\\nU.\\nC -J\\nI\\nCD\\nO\\n03\\nO\\no\\nCD\\n75\\nCO\\n03\\nc\\nc\\nc\\no\\no\\no\\n0?\\nCO\\nCO\\nc\\nc\\nc\\n03\\n03\\n03\\n*o\\nO\\n\u00e2\u0080\u0098o\\nO\\nO\\no\\nE\\nE\\nE\\nE\\nE\\nE\\no\\no\\no\\nO\\nO\\nO\\nCD\\nC\\nCD\\n\u00e2\u0096\u00a0g\\n\u00e2\u0080\u0098co\\no\\nX\\nLU\\n-O\\nO\\nO\\n-Q\\nE\\no\\nO\\nsi\\nto\\ns\\no\\nCl) 0)\\nT3\\nCO H\\nCD\\nCC\\nJ\\nCL O\\nO\\nCM\\nY CO CO CM\\nS3\u00c2\u00ae\\ny:\\n00\\ny y o\\n5 5\u00e2\u0080\u0099-\\nln 0 ^COCOM-0)lOCON r* MCMCOlt) TO)C5COOsy^M:- O^Cp [2COCMM MMSSn\\n^\u00c2\u00a7^^CM\u00c2\u00a7Sod z^coco--^coco CM CM\\nk CD O !f) C\u00c2\u00b0 Y Y CO\\nv-\\nCD\\n-C\\n-T\\no\\nCD\\nsz\\nO\\nro\\nc\\nCD\\n\u00e2\u0096\u00a0g\\nco\\nCD\\ncr\\nAppendix A National Emissions (1970 to 1998) A-23", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0223.jp2"}, "224": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n-a\\nD\\n3\\nC\\n\u00e2\u0080\u0099\u00e2\u0096\u00a03\\nC\\no\\nO\\nLO\\nI\\nJO)\\n.Q\\n(0\\n(opui tnoiT-offl tinN\\nO) Vo CM i\u00e2\u0080\u0094 VO CO\\nO)\\n(J)f)NCOinOOOCO in\u00c2\u00abnCO(0(0 J)(oC\\\\lo e OO if Wtft (MO)\u00c2\u00aeN tO)!DlOO\\nco vo m r- t- T* co m cm cm t- vo cm cm n 5i n cm\\nCD CM y\u00e2\u0080\u0094 t\u00e2\u0080\u0094 lo\\nVOO ^COO-r-OCOr K\\nvo CO T- 1- K CO\\ntO) tn\u00c2\u00aeT-OCDr NK\\nvo CM K CO\\nNc\\\\j 0(\\\\iCy^coc\\\\|iflnO) -voc\\\\i jNC\\\\j o\\nCM t\u00e2\u0080\u0094 O) CM CM VO T- 7\u00e2\u0080\u0094 Co CO CO\\ny- CO\\nt-Kco -cmocmcvjt-cocnjioco^covocmm-n.cmvovo\\nC\\\\| T- O) C\\\\| CM CO t- T- CO CD CO\\ny- CO\\nr ~VOcOVO\u00e2\u0080\u0099~-C)i\u00e2\u0080\u0094 CMr-r^CMVOCO^\u00e2\u0080\u0099\u00e2\u0080\u0094 VOC\\\\JM-VOv-COVO\\nCM O CO CM CM Co T- i-C\\\\|CO CO\\nCO\\nN CD CO t O\\nvo CM T-\\np O) m m- o\\nCM y-\\nCOCMt-C\\\\|COCMVOCDCOVOOcmOCMOCOCOoO\u00c2\u00bb~0 35^ 1 OCM 0-I\\\\Ko\\nt- 7 CM -M- Cm cm CM t CM t- 00 CO\\nCM\\nvo\\nONSO) CMCMlOinOlf)00 OCMffi OCONlflnO)KlOCM^\u00c2\u00bb00\\nCM CO CO CM CM o CM CMCO t- t- CO\\nT\u00e2\u0080\u0094 1\\nJO CO LO Tf\\nvo CM\\nf co in in\\nK CM\\nJo CO M M\\nvo CM\\nN vo cd in\\nK CM T-\\ni-Offl* OCMCl|t lOT-N tOoVOCMO VCON n051IOC\\\\|^\u00c2\u00a9COO\\nT-COrt cm CM V3) oil CM CO CM i- O I CM\\nT- VO\\nT-OOQN l OO|(OCOinCMtOOffl!OCMi- l \u00c2\u00aeCOoVOO)OIOIfl VtlOVOO\\nCM VO -M- CM 1 O) CM oo l- CM CM O CO CM\\nCM y- VO\\nT-oO CD M-CMV0C0C0CD 0 OCMC0CMO fs C0T-OoO |s M-V0 0-C0 0-O\\nCMVO-M- CMCMCDCM CO CM CM CM CO CO\\nCM 1 lo\\n-r-T-Tt^-o M-COVoKinCOlOCMCDlOCMOKCOCOCOCOCDCoK M-COCOloo\\nt- in CM in CM CM *o cm co \u00c2\u00b0o h~ cm\\nlo\\nCM^-OOinOOOOOOOpinCOCOCOVOCOVOVOCMOOOinCM M-in COV3)VOK M- M-COVOO\\nvo cm co m cm cm t-vo cmcm n o n cm\\ncm 1\u00e2\u0080\u0094 VO\\nOC)NitO)00000(OtO^COlOif 0 OCMOt )0(0 t tin CON\u00c2\u00aetOCOCOKlOO\\nlO t\u00e2\u0080\u0094 i\u00e2\u0080\u0094 CM M COcnCOCM t-VO CMCM COT VD Cm\\nCM t- vo\\nCOCT in T- CMjNoCMCOCOKcM rO c C T- Tr -VOCM Q OCOCOCM VOlO\\n03 ti-CM7tO77M^nCO KojKin NV0 7 M^So) TO l nVO CM CM\\nCD Vo T- co CM CO Tt Cm\\nco r^-JocDvo\\n\u00e2\u0080\u0098O5Nvri-P (o(o rn?i0)K C0K C0CM\\nk. Os rv fv I r\\\\ m rv /v i r\\\\ nr\\\\\\nCMCMn7C077C0^CMV0C0 CMN0)KS MN 7 inin CMNoiM\\nVO CM CM CO t\u00e2\u0080\u0094 lO CM\\nCO\\nlo -M- CM\\ncm\\nCM\\nCO\\nJO CO 1- CD\\njn M (D 7 M-\\nN\\ntovoncocoQKm Nffinvo CT)0)TsCMmNKU)ioioO)Co\\n77 (D! O)SlOCMNO)VOVo9ciieo$0(\u00c2\u00a3)9^tOllOin^ CM co\\nco m co t- m cm cmco M\u00e2\u0080\u0099Cm\\nlo\\n2\\nK\\no\\nQ\\no\\ncc\\n0\\nQ\\nUj\\n-J\\n\u00e2\u0080\u00a28\\n-J\\n3\\nCD\\n5 I\\n2 i\\n_ CO\\nCO o\\nE E\\nE D\\nCD SZ\\nsz o\\no O\\no C\\nc co\\nCO CD\\nE o\\nO\\nCD\\n2 co\\n2\\nc\\nco\\nCD\\ncc\\noS\\nL_\\nCD\\nE\\no\\nQ.\\no\\nE\\nCD\\nx:\\no\\nco\\nk_\\n3\\n3\\no\\n*w\\nCD\\nCD\\nCD\\nE\\nCO\\nc\\nUJ\\nkT\\nD\\nD\\ncr o) O)\\nSoil\\nO)\\nc\\nco\\nCO\\na\\no\\no\\nCO\\n\u00e2\u0080\u0098c\\nI\\nc\\nCO\\n3 fc\\nCD CD\\no _c\\nco o\\nE\\nC3\\nCO 3\\nLU i\\no\\no\\nCD\\nsz\\ncl a. O\\nDC\\n0\\n0\\n-J\\n5\\n25\\n(O\\n13\\no\\nl\u00e2\u0080\u0094\\nl\u00e2\u0080\u0094\\no\\nc\\no\\nc.\\nQ)\\nI\u00c2\u00ab\\no -9;\\nO)\\nc\\n(0\\nCO\\na)\\no\\no\\nqI\\nJO\\n03\\nCD\\nV\\n-C 3\\no 2\\n5\\no\\nLU\\nCD\\nc\\nCD\\nCD\\nCD\\no\\no\\nN\\no 2\\nC q za\\nQ. vo o w\\nCD\\nUJ\\nEE\\n1\\nQ\\nEi\\nUJ\\ncc\\nI\\nUJ\\n-4\\no\\nUJ\\na.\\n10\\nCD\\nCO\\n3\\n\u00e2\u0096\u00a0U\\n_c\\n\u00e2\u0096\u00a0O\\n0\\nto\\nCD\\nDC\\no3\\nCO\\nCD\\nc\\no\\nO 0)\\n3 c\\n\u00e2\u0096\u00a0O\\nO CD\\na; cn\\nCO E\\nCO 3\\no\\noa 2\\nr= 0\\nO 0-\\nW)\\nc\\n3\\nCD\\n.c\\n\u00e2\u0096\u00a05\\no\\n5\\no\\no\\ns\\n2\\nco\\no\\n\u00e2\u0096\u00a0O\\n3\\n0\\nUJ\\n0\\nfo\\nUj\\no\\nCD\\n\u00e2\u0080\u00a2E 5\\n3\\nm S\\n3 5\\nc S\\ni 5\\ns\\nQ. OC\\nco Uj\\nI\\np\\no\\no\\n3\\n\u00e2\u0096\u00a0D\\no\\n-O\\nCD\\nV_\\n~o\\nc\\nk\\nofl\\nrT\\no\\no\\n0)\\nco\\nLi- *0) 0 JO\\nQ) c\\nt= c: k\\nJO\\nJO\\n1\\n.c\\n5\\nCD\\no\\n3\\n-O\\no\\n0.\\nCO\\na.\\nCL\\n\u00c2\u00b0C\\nbT\\nCD\\ns:\\no\\nu\\nk_\\nCO\\n5 g TD\\nS m\\nCD\\nCD CD\\nvo\\nCO\\nCD\\nc c\\nco 5\\n5 nj v- v\\ni Q) J! 10\\no -s\\no o\\nCD\\n.VU\\nA-24 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0224.jp2"}, "225": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nTJ\\nd\\n3\\nC\\nm\\nC\\no\\nin\\nQ)\\nA\\n(0\\nin\\n,_\\n00\\nCO\\no\\nK\\n05\\noo\\nin\\nM\\n\u00e2\u0096\u00a0M-\\n05\\nCO\\nT\u00e2\u0080\u0094\\nCO\\nC3\\nCO\\nCO\\nCO\\n05\\nN\\n05\\n1^\\nV)\\nCM\\nCO\\n05\\nCO\\nt\u00e2\u0080\u0094\\nCO\\noo\\n05\\n05\\nCO\\nCO\\no\\nK\\n05\\n\u00e2\u0096\u00a0M\\nCM\\nT~\\nO\\n05\\nCO\\n1r\\neg\\n05\\nC5\\n05\\noo\\nCO\\nlo\\n05\\ne-\\nin\\nCM\\nM-\\nY-\u00c2\u00bb\\n05\\nCO\\nT\u00e2\u0080\u0094\\nT\u00e2\u0080\u009c\\nT~\\nK\\no\\nrv\\n05\\n5\\nCM\\nCM\\nO\\nY*\u00c2\u00bb\\n05\\nCO\\nT_\\nO\\nin\\ncp\\nr-.\\n03\\nuo\\n05\\no\\n00\\nco\\n05\\nr\u00c2\u00ab*\\n05\\nCO\\no\\non\\nv\\nrc\\no\\nv\\no\\nk.\\n3\\nO\\nCO\\nS\u00e2\u0080\u0099$^ Tt ScM^^S C 0 OOO (\u00c2\u00a3)OT OWOOO 2 O,_OO _OT O OQO\\nCM\\n03\\n03 CM CO\\n538 5 Sj\u00c2\u00a3 3 0 O 0 \u00c2\u00b0-\u00c2\u00b0^\u00c2\u00b0\u00c2\u00b0O S O,-OO^OOOO\u00c2\u00a3 \u00c2\u00a3OOO\\nTt S^^^^ 00 OOO g\u00e2\u0080\u0098 OO OOO \u00c2\u00a7\u00c2\u00b0OOO T -OOO fe ^^OQO\\n5 w nN \u00c2\u00a7^Srl Nooon OOOinr H! OOOOT OT o o S 0QQ O\\nCO 05\\nV) 05\\neg\\neg\\neg\\neg\\nCM\\nz z\\nT- N O\\nS\\n7 7\\no\\nT- O\\nO CO K\\nO CO K\\nt- Co N ~i\\no in o in o o o\\n1 Co 00\\nO O) N O O O\\n03 CM K\\nco i?S3 Ti Tl l Z 0) ocM coCMooocMO t Ooo \u00e2\u0080\u0099-oo o T ^ro\\nOKCO 03 *o eg zzS z 12 Z\\nco f S tciS\u00c2\u00a9!o(0(j)o\u00c2\u00ab gC iooowo ^ooo roo o)C^(o ro\\nONC 0 0003 10 2 w ZZS z 2 O5C0CO\\n\u00e2\u0096\u00a0^r S coT-coc)egcocoocg ooCMoooego f -ooo ^oo Lncoc\\\\|r-.rq-o\\nO N CO O c\\\\j lo CM ;7 7 O C^ K\\nT- Tt eg \u00e2\u0080\u0098C- c T~ *0 t-\\ncd^ ^^co^cm^ios^zzzzZzzzzzzzZzzzzzzzzzZZZZz\\nM-CO O C\u00c2\u00bbCO\u00c2\u00bb\u00c2\u00ab00K\\nh^^ 7 \u00c2\u00a9Pl; 9 57 ZZZZ?ZZZZZZZ 2 ZZZZZZZZZ 222 ?Z\\nCM CM\\noo K 10 lo\\n0 \u00c2\u00a3Sk S S SSSS\\nW O\u00e2\u0080\u0098 07 CMpC 0 |fiO Z 7\\nZzzzzzzzZzz\\nZ Z Z Z Z Z Z\\n\u00e2\u0096\u00a0O\\nD\\n3\\nc\\nc\\no\\nCJ\\n0\\nUj\\nCO\\n\u00c2\u00abo\\nUJ\\no\\no\\noc\\nco\\no\\nD\\n*o\\no\\n2\\n05\\nc\\n1c\\ns\\n3\\n0- C35\\noQ\\nw- 9\\n15 3\\na. Q.\\n03\\na.\\n03 5\\nIs.\\n3\\n2\\n\u00e2\u0096\u00a0O 3 S\\no w o\\no\\no\\n3\\n\u00e2\u0080\u00a2O\\no\\nk_\\n0.\\no\\n0\\nCO\\n0\\n13\\no\\n0\\nc\\nJ5\\n0\\no\\n0\\no\\n.c\\nCO\\nCO\\n0\\n0\\no\\n13\\n*o\\n2\\na a.\\n2\\nS g\\n\u00c2\u00a3T S\\nc\\nS .2\\n5 E\\n0)\\no\\nJO\\nE\\n03\\no\\n3\\nc/3 c/3\\n3\\no-\\n03 l.\\nC 03\\nO\\n5\\ns E\\n-O 9\\nO 3\\nJr O-\\n0 lu\\n.2\\n03 C\\ng o\\n-5\\nCO 03\\n2 lD\\nc\\n03\\nE\\ng.\\n3\\nCT\\nUJ\\n.a c\\n.2\\ntj\\no\\nQ. \u00c2\u00b1r\\n2 c/3\\n5 c\\nCO o\\nI- o\\nc/3\\n03\\nCO\\nCO\\n03\\no\\no\\nk_\\nCL\\naj\\n0\\n3\\n\u00e2\u0096\u00a0O\\njz\\nCO\\nD\\no\\n0\\nc\\n03\\n0\\no\\n0\\n2\\no\\np\\n-J\\nC3\\nK\\nz\\n-I\\no\\nc/\\nCO\\n03 t\\nC\\nCO\\n\u00c2\u00abJ _\\n03 -C\\na.\\nQ\\n05\\nc\\np TO\\n9 o\\nO\\nCO\\n05\\n.55\\n\u00e2\u0096\u00a0t; 15\\nCD\\n03\\nO OS\\nfc* 3\\nQ W\\no CC\\ng\\nc CO\\n.2 Z\\nn oc\\nR\\n5 08\\nCO\\nc\\nja\\nCL\\n03\\nJO\\n00\\nc\\n\u00e2\u0096\u00a0e\\nCD 2\\n03 o.\\nCO\\nO CO\\nCO H\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094* \u00e2\u0080\u00a24\u00e2\u0080\u0094\\no o\\n3 Z)\\nO D\\n2 2\\nCL 0.\\nE E\\n3 3\\n03 03\\nO O W\\n03\\nCL\\nofl o8\\nE E\\n05\\nn\\no O\\no\\nCO\\nCO\\nc\\no\\nD\\n1 S\\nCO\\no o\\n03\\nOL\\n03\\n0.\\nCO\\nc\\no\\nra\\nCO\\nCD\\no\\n0\\nCO\\ntr\\n0\\n\u00e2\u0096\u00a0c\\no\\n0\\no\\nO)\\nCL\\nO)\\nCL\\n0\\nC /3\\n0\\nl_\\nC /3\\nk_\\nC\\nc\\no\\nCS\\nO\\nCC\\nl_\\nCO\\nk_\\n1\\nCO\\n1\\n_\\n0\\n1 c\\n0\\n0\\no\\no\\no\\ng\\nE\\nE\\nE\\nE\\n0\\n0\\n0\\n0\\n-C\\n-C\\nsz\\n_c\\nO\\nO\\nO\\nO\\no\\no\\no\\no\\n\u00e2\u0080\u0099c\\nc\\n\u00e2\u0080\u0099c\\n\u00e2\u0080\u0098c\\n0\\ncS\\n0\\n0\\nO)\\n03\\no\\nk_\\nO)\\nk_\\nL_\\no\\no\\nO\\nO\\nc\\nc\\n03\\n03\\nCO\\nk\u00e2\u0080\u0094\\no\\nCO\\no\\nTO\\no\\nCD\\nT3\\n3\\nc\\nO) p.\\nCO 2 -o\\np\\nCO\\n1\\no\\n\u00e2\u0096\u00a0c\\no\\nQ-\\nco\\nc\\nCO\\nJO\\nCO\\nL\\n03\\nCO\\n3\\nCD\\nAppendix A National Emissions (1970 to 1998) A-25", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0225.jp2"}, "226": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nO\\nD\\n3\\no\\nin\\nI\\nQ)\\nn\\n(0\\nl-\\nCO\\n3\\nT\u00e2\u0080\u009c\\nco\\n2 P\\nCO\\nK\\n00\\nO\\no\\no\\nCO\\nK\\nCO\\nCO\\no\\no\\no-\\nNy\\noo\\nCM\\no-\\nCM\\nco\\nT\\n00\\nco\\nY\u00e2\u0080\u0094\\nC 5\\nY\u00e2\u0080\u0094\\nC 3\\nCM\\nY\u00e2\u0080\u0094\\nCD\\nCD\\nCT 5\\nv~\\n05\\nCO\\nCM\\n05\\nYy\\n12\\nLO\\nCO\\n\u00e2\u0080\u00a2M\\nCM\\nYy\\nLO\\nM\\nCD\\nY\u00e2\u0080\u0094\\n05\\nT\u00e2\u0080\u0094\\nCO\\nCM\\nY--\\nCM\\nY\u00e2\u0080\u0094\\nyct\\nr-\\nK\\nO\\nco\\n2 P\\nCO\\n12\\nCO\\nO\\no\\no\\nCM\\nY\u00e2\u0080\u0094\\nIN\\nCO\\nCO\\no\\nY\u00e2\u0080\u0094\\n12\\nK\\n05\\n00\\nCM\\nCO\\nco\\nCD\\nCO\\nY--\\n3\\nCM\\n3\\nCM\\nY-\u00c2\u00bb\\n3\\nCD\\n05\\n3\\n05\\nCO\\nCM\\n05\\nY~\\nNy\\nCO\\nco\\n\u00e2\u0096\u00a0M-\\nCM\\nYY.\\nco\\nCO\\nLO\\nY-*\\n05\\nCD\\nCM\\nY^\\ncm\\nY-y\\n*t\\nCD\\n05\\nCM\\nK\\nM-\\nN\\nO\\no\\no\\nCM\\nHi\\nin\\nco\\nC 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3\\n00\\nCD\\nY\u00e2\u0080\u0094\\nCD\\nCD\\nr-\\n05\\n05\\n05\\nCM\\nCM\\nCO\\nN\\nY\u00e2\u0080\u0094\\nfY-\\n|Y-\\nN.\\nK\\nz\\nz\\nz\\nz\\nz\\n\u00e2\u0080\u00a2o-\\nCM\\nCM\\nIN\\nCM\\nM-\\nCM\\nT\\nCO\\nco\\nYy\\n5\\nCM\\nCM\\no\\ncn|\\no\\n4\\nCD\\nO\\na)\\no\\nw.\\n3\\nO\\nC3\\n2\\ng\\nid\\ncc\\n-J\\nCO\\no\\n0\\nCO\\nQ\\ntf\\nCO\\nc\\n:o\\nS)\\n2\\no\\nc\\n2 m\\nc\\na\\nCL\\nO\\n\u00e2\u0080\u00a22\\nc\\n75\\n2\\n0\\nXD\\no\\na\\nu\\n4\\n(D\\n03\\n.S5\\nu\\nC0\\n3\\nT3\\nC\\n(J)\\nB\\nc\\n03\\nUJ\\nd\\ni\\nQ\\nO\\nCC\\nO\\nc/5\\n0\\no\\no\\nk_\\no\\no\\n\u00c2\u00b0s\\nw\\no\\no\\nx:\\n2\\n03\\n0\\n3\\nQ\\n.c\\n05\\nw\\n-2\\n,o\\n-c\\nc/5\\n2\\no\\n3\\n0\\n05\\n1\\no\\no\\n2\\nt/\\no\\n3\\nw.\\nI-\\nC/5\\nCD\\nCD\\n3\\nQ\\nCD\\nic\\no\\n3\\nCO\\n2\\nO)\\na\\nCM\\nQ\\n2\\nCO\\n2\\n05\\n\u00e2\u0096\u00a0O\\n-c -c\\n.05 .05\\nCO\\nas\\no\\nLc\\n05\\nCO\\nCD\\nO\\n3\\nQ\\nI\\nr\\nCD\\n05\\nX\\nco\\n05\\nO\\n-C\\n05\\nCO\\n05\\n6\\no -c\\n2\\n05 05\\nCO CO\\n05 05\\n6 \u00e2\u0080\u0099S\\n-g\\nV o o\\n|2 2\\n05 O)\\n\u00c2\u00ab0\\nUJ\\n-J\\no\\n1\\ni\\nCO\\nUj E\\no\\ng\\nS\\nQ\\nO\\nCC\\n2\\nO\\nO o\\no\\n2\\ntr o\\n2 8\\no\\nc\\n.o\\n4\\no\\n2\\n4\\nCO\\ng\\no\\nc\\nI\\n2\\n.2 05\\n*5\\ni\\nI\\nc\\nca ca .y\\n.o\\n2\\n05\\n2\\n2\\no\\no\\n4\\n05\\n05\\nO\\nc\\nCD\\nC\\n.8 3\\n2\\n05\\n_ C/5\\nC t\\n05\\nO CD 05\\nID C t\\n05\\n-C\\n05\\n05\\nCO\\nCO\\n05\\n.C\\nc\\nCD\\nc\\n5\\n2\\n1 i\\no\\nA-26 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0226.jp2"}, "227": {"fulltext": "National Air Pollutant Emission Trends 1900-1998\\n~a\\n0\\n3\\nC\\n\u00e2\u0096\u00a04-\\nc\\no\\nin\\n0\\nn\\n0\\no\\nu\\n0)\\n4-^\\n(Z\\no\\n0)\\no\\n1-\\n3\\no\\no\\nCD\\nCT)\\nCT)\\nCM\\nI s\\nCT)\\nCM\\nT3\\n0\\n3\\nC\\n*5\\nC\\no\\nC\u00c2\u00a3\\n0\\nUJ\\n-J\\nO\\ns\\ni\\nUJ\\nes\\ns\\nQ\\nO\\nQC\\nO\\nO t O) lo Co\\nCo XJ- cb\\nCO o p 00\\nXj- N*\\nK O) Co C\\\\1 rj- oo\\nYt Co 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s\\nco\\nr-\\no\\nSi\\ns\\nCM\\nCD\\nz\\n00\\nz\\nm\\noo\\nCM\\ntJ-OCMCDCDCoKCM\\nO O) CM CO y\u00e2\u0080\u0094\\nCM\\no r id o\\n3 CM y-\\nCOCD TOO T T^T t? ^^:CT)\\n2 co\\nCO\\n\\\\fOO)COCD OIO^O T T -CT)\\nLO KCD y- y\u00e2\u0080\u0094 2 2 CM\\n5 CM\\n.0\\n0\\n0\\n0\\n0)\\no 0\\n0)\\n0 m\\n9 c\\nb .o\\n2 0\\ng a\\noc y\\n0\\nc\\no\\nc\\n0)\\nC T)\\n.6 S\\nO 0 O)\\n2 S oa\\n0\\no -S\\ni\\n0\\n03\\na\\n0)\\n6\\nE\\no\\no\\nc\\n03\\nC\\nCD 0\\na C\\n03\\nc\\n03\\nS\\neg\\nc\\no\\n5)\\nm 0\\n1 a\\ne-l y\\n0\\nCD\\ncn\\nc/)\\n0\\nO\\n0\\n0! C\\nQ) s -q\\n0\\nx:\\ns 5 0 a a\\n0 s 0 2 s\\n0 C O a- 0 2 O\\nO O 2. t.\\n0\\n2\\nO)\\n0\\nGC\\nO\\n0\\no\\nGC\\nI\\nc\\no\\nz\\n0\\n5\\nC3)\\n6\\n3\\n0\\n8\\n0\\na\\n\u00e2\u0096\u00a0o\\n0\\n3\\no-\\n0\\ns\\nO)\\na\\n3\\n0\\nc\\n\u00e2\u0096\u00a0O\\n0\\n0\\n0\\na\\n9-\\nS -j\\nHi\\no\\no\\n3\\n0\\nQ. 0\\no y\\nI\\nI\\nc\\no\\n1\\no 0\\nc 8\\n0 .c\\nO) S\\no s\\n0\\no\\nO\\n-i\\nJ\\nUJ\\no\\nCO\\n0\\n0\\nv_\\no\\nLi-\\n03\\n0\\ni_\\n3\\n3\\no\\n*c\\nO)\\no\\n3 3\\nC\\no\\n3 3\\nO O\\nc c\\n0 0 1\\n0 0 0\\nL\u00e2\u0080\u0094\\nD\\n5\\n.o\\nw\\n3\\nJO\\no\\nO o)\\no\\no\\no\\nAppendix A National Emissions (1970 to 1998) A-27", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0227.jp2"}, "228": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n00\\n03\\n00\\nCO\\nco\\nCO\\nT\u00e2\u0080\u0094\\n03\\nCO\\nT~*\\nM-\\nt\\nO)\\nS\\nCO\\nCO\\nCO\\nK\\nT_\\no\\nC\\\\T\\nc\\\\T\\nM--\\no r\\nCM\\nco\\n3\\nS2\\nCO\\nCD\\nO)\\nO\\nCO\\nco\\nCM\\n1\u00e2\u0080\u0094\\nCM\\n03\\nCO\\nco\\nCO\\no\\nK\\nCM\\n03\\nCo\\nc\\\\T\\nM--\\nT\\n,f\\nT\u00e2\u0080\u0094\\nCO\\nCO\\nLO\\no\\nC3\\n00\\nCO\\n03\\nh\\nCO\\n05\\nK\\nM-\\n03\\nCO\\no\\nCO\\nco\\nco\\no\\nT\u00e2\u0080\u0094\\nCO\\nC\\\\T\\nc\\\\T\\nco\\nCO\u00c2\u00ac\\nCO\\nLO\\nCO\\nC\\\\|\\n05\\nM-\\nCO\\no\\n03\\nCO\\no\\n00\\n1^\\n03\\no\\nCO\\nCO\\nco\\no\\nT\u00e2\u0080\u0094\\nK\\no\\nc\\\\T\\nCO\u00c2\u00ac\\nK\\nT_\\nCM\\nTf\\nCM\\no\\noo\\nCO\\n05\\nCO\\n03\\nCM\\nN\\nCO\\nM-\\nCO\\nT\u00e2\u0080\u0094\\n03\\no\\nco\\nCM\\nco\\n05\\nctT\\nc\\\\T\\nCO\\nO\\n1\u00e2\u0080\u0094.\\nCO\\nCO\\n3\\nc\\\\j\\n05\\nCO\\no\\nLO\\nCO\\nCO\\nJO\\nO\\nO\\n03\\n\u00e2\u0096\u00a0c*\\nCO\\nM-\\nCO\\nT\\nco\\nT-\\ncvT\\nco\\nT\u00e2\u0080\u0094\\nCM\\nCN\\nCo\\nCO\\nco\\n05\\nCM\\n03\\nr-\\nT\u00e2\u0080\u0094\\nM\\nCO\\nCO\\n03\\n3\\nM-\\nM-\\nCO\\no-\\nco\\nCJ-\\nC\\\\T\\ncn\\nT\\nCM\\nCO\\nCO\\n05\\nM\\nN\\no\\n03\\nr^\\nC3\\n25\\n05\\nK\\nco\\n03\\nN\\nCO\\nO\\nCO\\nin\\nT\\nco\\nc\\\\T\\nM--\\n05\\nT\u00e2\u0080\u0094\\nCM\\no\\n03\\nCO\\n05\\nCO\\nCM\\n03\\nCO\\nCO\\nM-\\nM-\\nCO\\nCD\\n03\\nC3\\nC\\\\J\\nCM\\nCM\\nCO\\n05\\nT\\nco\\ncm\\nM--\\nO)-\\nT5\\n0\\nMM\\nT\\nCM\\n03\\n03\\nco\\n05\\n05\\n25\\nO\u00e2\u0080\u0099\\n3\\nCO\\nCM\\nip\\nCO\\n05\\nCO\\nC\\n03\\nCM\\nN\\nK\\ncm\\nCO\\no\\n\u00e2\u0096\u00a0MB\\nT\\n03\\ny\u00e2\u0080\u0094\\nCO\u00c2\u00ac\\nv\u00e2\u0080\u0094.\\nco\u00c2\u00ac\\n4^\\nCM\\nT\u00e2\u0080\u0094\\nco\\nc\\no\\nCO\\nOi\\nCO\\nCM\\nCO\\nCM\\nCO\\nco\\nK\\no\\nCO\\nr^\\n03\\nCM\\nco\\n05\\nco_\\nCO\\no\\no\\n\u00c2\u00abM\\nCO\u00c2\u00ac\\nt\u00e2\u0080\u0094.\\nin\\n1\\nCO\\nT~\u00c2\u00bb\\nCO\\nLO\\no-\\nCO\\np\\n25\\nCO\\n00\\nCO\\nCo\\nK\\nCO\\n\u00e2\u0096\u00a0o\\nq\\n03\\nco_\\no\\nCO\\nCO\\no-\\n03\\nT\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nco-\\ncm\\nco\\nn\\nCM\\nY~\\no\\n(Z\\ni\u00e2\u0080\u0094\\no\\ns\\ns\\ns\\n05\\nl\\n00\\n03\\nZ\\nt\\nLO\\ns\\ns\\nT\u00e2\u0080\u0094\\nI s\\n03\\nz\\ns\\ns\\nr-\\no\\nT\\nK\\no\\ns\\nCM\\n03\\nz\\nO\u00e2\u0080\u0099\\no\\nCO\u00c2\u00ac\\nET\\n0\\n3\\nC\\nc\\no\\n4c\\nCO\\no_\\n0\\nUJ\\nP\\n4t\\nI\\no\\nk.\\no\\np\\no\\nto\\n0\\n8\\n\u00e2\u0080\u00a2Q\\n8\\nc\\no\\n\u00e2\u0096\u00a0Lr\\nO\\ncc\\no\\nOl\\n0\\nUl\\n2\\n3\\nQ\\ns\\n8\\nk\u00c2\u00ab.\\nn\\n4-*\\n0\\n0\\na\\nw\\nc\\n0\\n_l\\n_l\\nO\\nc\\n0\\no\\n3\\na\\no\\no\\n0\\nUj\\n03\\n_l\\nO\\nk.\\no\\n3\\nLL\\nft\\n3\\nCO\\n1\u00e2\u0080\u0094\\nO\\no\\n0)\\n1-\\n0\\nw-\\no\\nE\\n0)\\nsz\\nO\\n0\\nC\\n0\\nc\\no\\no\\nD\\nk_\\n0\\nD\\n.a\\n0\\na\\nT3\\n0)\\n0\\nCD\\nT3\\nd)\\nO\\nE\\n33\\nJZ\\n0\\n0\\nH)\\n0\\n\u00e2\u0080\u00990\\n0\\no\\nc\\na)\\nu_\\n03\\nLO\\n00\\n03\\nCD\\nC\\n\u00e2\u0080\u0098c\\nc\\n\u00e2\u0080\u0099O)\\nX\\nk_\\no\\no\\no\\nu\\nQ.\\nk_\\n0\\nX\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094\\n0\\n0\\nc\\no\\ng\\nE\\n0\\n0\\n0\\no\\nO)\\n03\\n0\\no\\n03\\no\\nk_\\n13\\nO\\nC/3\\n0\\nk_\\n03\\n03\\nCO\\nCO\\n.03\\n5\\n03\\n03\\n-4\u00e2\u0080\u0094\u00e2\u0080\u0099\\n0\\nO\\n03\\nC3\\nV\u00e2\u0080\u0094\\nO\\no\\nC/3\\ng\\no\\n03\\nCl\\nCO\\nco\\n05\\no C/3\\nCM\\no\\n03\\nC3\\nJC\\n03\\no\\n03\\nTO\\n03\\nc\\n\u00e2\u0080\u0099c\\n3\\n\u00c2\u00ab3\\n03\\nO\\n\u00e2\u0096\u00a0O\\n03\\n5\\no\\nO\\nco\\n03\\n5\\nk\u00e2\u0080\u0094\\no\\no\\no\\n\u00c2\u00ab3\\n03\\n05\\n\u00e2\u0080\u00a24\u00e2\u0080\u0094\\no\\nc\\n32\\n3\\no\\no\\n0\\nX\\n0\\nc\\no\\n0\\n0\\nE\\n0\\nc\\n0\\n\u00e2\u0080\u00a24\u00e2\u0080\u0094*\\nc\\no\\no\\nCO\\n03\\nX!\\n\u00c2\u00b0s\\nIt\\n0 X;\\nI i\\n;g\\nCO CO\\n33 C\\no\\nII\\nII\\n.9 T 3\\nc co c\\nCO C/3 CO\\n03 p /3\\n^5 0\\nc\\no\\n\u00e2\u0080\u00a2e -c\\no .01\\no-\\nC CO\\nCO 03\\n-C r-\\n6\\nLL\\n03\\n0 t; co\\n5 g\\nM O\\n(C 0 O)\\n00\\n03 03 O\\nO 0\\nC Ol-L\\n11 2\\nI 2P\\n.w,\\n03\\nO\\nCO Q)\\n2c\u00c2\u00bb\\nco\\nc E\\na) jc a)\\nCO 0\\n21 0\\ng\\n8\\n||o\\nCO o\\n2 o O\\nQ3 o\\nN 2\\nco\\nc\\no\\n03\\n03\\n00\\no\\n03\\nO\\n5\u00e2\u0080\u0094\\n3\\no\\n0\\n0\\nE\\no\\nL_\\n0\\nC\\no\\n\u00e2\u0080\u00990\\n0\\nE\\n0\\n0\\n0\\n0\\n0\\n0\\n0\\n3\\nc\\nc\\n0\\n33\\n_\\nCL\\nk_\\n0\\nc\\no 2\\n\u00e2\u0080\u00a24 1 L_\\n\u00c2\u00b10 9\\n3 (/5\\ng co\\nE E\\n\u00e2\u0080\u009cO Q3\\n03\\n03\\n0\\nE\\nco\\nk_\\nCD\\n0\\n03\\n\u00e2\u0080\u0098CD\\nO\\n0\\nc\\no\\n0\\n0\\n0 2\\nII\\nI\\no\\nCl\\nII\\nW\\n.52 1\\n-C Q3\\nc 0\\n\u00e2\u0080\u00a2O\\n03\\n*0\\n_3\\no\\nc\\n0\\nk_\\n0\\n0 o\\nS\\nCO 0\\n.52 5\\nE 03\\n0 _\\nc\\no\\nw -c\\nO 03\\n0\\no\\n0\\n3\\n-4\u00e2\u0080\u0094\\n0\\n0\\nX\\n4\\no\\nE\\nCM\\nc\\n0\\nk\u00e2\u0080\u0094\\n3 D\\n1|\\nE\\n0 .55\\n0\\n03 -3\\n_ O 3\\ns c E\\n5\\n-P 0\\n3\\n0\\nk_\\n0\\n0\\nc\\no\\n0\\nc0\\nE\\n0\\n0\\n0\\n0\\no\\no h-\\no\\n0 *_\\nJC C\\nCL 3\\n0 O\\nE\\n0\\no\\nE\\n0\\na. c 2\\no E\\nO 03\\n2\\n0 0\\nQ. C\\n3 03 0\\nO D 03\\n-2 -03\\n0 0\\n5I 3 jz\\n-o\\nc\\n3\\nO\\n0\\n3\\n(J)\\nC\\nX\\no\\nk_\\n0\\n0\\n0 -b\\n5\\nt! *o\\n0 CD\\n0 .ti\\n0 0\\no\\n0\\na\\n0\\n2 5\\nc\\n0 0\\n0\\no g\\np 0\\ni 0\\n5\\n0 .52\\n0 jE\\nc\\nQ o\\no\\n-c\\no\\nCL\\n0\\n0 jd\\no\\nO)\\nL.\\n0\\nc\\n0\\nc\\no\\n0\\nc\\n0\\nCL\\n0\\n3\\n\u00e2\u0096\u00a0O w\\n0\\nO .n:\\nE\\n2 T3\\n0\\nc\\ng\\n0\\nc\\no\\n0 o\\n0 0\\nE -S P\\n0 E\\n0\\n0 3\\n0\\n0 0\\n0\\n0\\n3\\nk-\\no\\ng ^5\\n12\\n\u00e2\u0080\u00a23 g\\nE 5\\n0 0\\nS 5\\no 0\\n0\\n03 _\\nn 3\\nO)\\nif\\n0\\nr e\\n_ 5^\\n0 c 1 3\\nw 0 cL\\nE -c o 0\\n\u00e2\u0080\u00a2^0 3\\n0 \u00c2\u00ab-E\\no 0 0\\nE g 0\\n-1 o\\nCL \u00c2\u00a32 0 g\\n3 13\\nL_ TO 0\\nffl 0 2\\no 0 2\\nco 3 E\\nQ 3 0 o\\n0 N\\nf\\nfa\\no E\\n0\\n03 ff\\nc\\n0 0\\n0 P\\no E\\n0\\n0 -O\\n3\\n0\\no\\n3\\nO\\nif)\\nC\\n03\\nE\\n0\\n.c\\n0\\nW\\n0\\n0\\n0\\nk_\\n03\\n4\\na. 03\\n0\\nx\\n0\\nk_\\n0 _ _\\ncd 0 g\\n11\\n2 O\\n03 0\\n(f)\\n0\\nX\\nH\\n0\\nO\\n0\\nQ-\\nif)\\nC\\no\\nA-28 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0228.jp2"}, "229": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nC\\no\\nMB\\nLU\\n00 co 00 c\\\\j If) 00\\no) o cn O)\\ncn\\nD\\nU\\nCO r\\no\\nfel\\n0-\\n0 S\\nts g\\nE\\nLU\\n4-\u00c2\u00bb\\no\\nD\\nCO\\n0)\\no in o io lo\\nJ) *0 CO (*5\\nCD\\n0)Q^co\u00c2\u00aboc\\\\inro too)io^oo l ooiO t\\ny\u00e2\u0080\u0094 VO OsJ C\\\\J t\u00e2\u0080\u0094 ror\\\\ir- rn LTi\\nCO C\\\\J\\nCD CO\\no\\no\\nTf I 00\\n1\\nr* t\\nm rt-\\nco co\\nco co\\noo^- tO)Cooc\\\\iTto i t\u00e2\u0080\u0099 0)in\\nt- CO CM T CNJ CNJ CO CM\\nT~ CD U} T\u00e2\u0080\u0094 Co h-lOTtr-T\u00e2\u0080\u0094\\nn CO CO\\nfo CO S CVJ CO Tt\\nWi CO CO C*J T-\\nCO!OTfd)COQC\\\\|(\u00c2\u00a3)(M fOO)lfl IOClKO\\nT- Co CM t~ CM M CO^M t CD CO\\nOmNcDIONt-COOOiOIO\\ni- co co t- f- t-\\nio\\nKcD^oinco cx\u00c2\u00bbcoinci co\u00e2\u0080\u0099~c\\\\jcoxf M-\\nO 00 CO c\\\\( 7 T- O N M A1\\nCM\\nTtttioococoocococDcDincoco^^c\\n*t cm men Tt co O .oooot?\\ncn\\nS co oo\\nO- M\\nn\\nco cd m- K in in\\nO oo CO\\nI^COinOOCOOCMCDCM O-\\nr- to CO CM CM\\nCM\u00c2\u00ae ct-Oo l 0O 0 roO(Din(DCM(D\u00c2\u00a9\\ncm coin cm co\\nCO Tj* Tt\\nin\\ncm o n. co in m\\nQ) U T\\nCM rf O C \\\\1\\nI s cm cm\\nCO I** CO M-\\nCM c\\\\j\\nt- to co o ro oo\\nt}- CM CO *0\\nr-CO Oin(DCMM t\\n\u00e2\u0096\u00a0\u00e2\u0096\u00a0-CO h* CD CD 7\\nCO Tt -M- \u00c2\u00a3l\\nin\\n(ONCOOO OM CDO)cnO\\nO CO CO 9 T- Co CM C\\\\|\\nO CO CD CM co\\ncm cm\\nncocooroMOM-oCMfflincocMcocorfin\\nco cm mio -r- co n in in\\nco\\nin in\\nio in co co co\\nQ CO If)\\nm in co co\\n7 T- lo CM\\nco CO cm co\\nCM CM\\nco o o co in o\\nco cm T in *o\\nco\\no?(Dinincomin\\nt- co r* co co a\\nco in in\\nin\\nN O) M 1\\nCM O) CO\\ncp in\\ncm\\no\\nCM\\nCT) CO CM\\nCM CM\\nCO t- CO M\u00e2\u0080\u0099\\nCO CM\\nCD Oi\\nCO CM\\nO CO CO\\nf CO\\nm- in\\ns\\nco in in co t-\\nr~* o o\\nin in\\nin\\n0 CO\\nO co\\nO O CD\\nP\\nUj\\nCQ\\nS\\no\\nO\\nUJ\\n3\\no\\nS|\\na\\n3 -Q\\n-t 3\\n-Q co\\na\\n.1\\na\\no\\n5\\n-c\\nC\\nco\\nco\\no\\nO\\nco\\nCO\\no o\\nc\\no\\n00\\n3\\nXI\\nE\\no\\nO\\n75\\nc\\ni_\\n0\\nc\\ns\\nis\\nI\\nOQ\\n5\\nO\\nO\\nUj\\nCO\\n3\\nO\\n3\\no E\\na\\nE 5\\n3 -Q\\n\u00e2\u0080\u00a2ts 3\\n\u00e2\u0096\u00a0Q CO\\n0)\\nC\\n.05\\n\u00c2\u00b0e\\n0)\\no\\ncn\\nCD\\nO\\nco B\\nss\\nCO\\nE -6 O\\nCD\\n9 a\\na o\\nco\\no\\nO\\nco\\nCO\\na\\nCD\\nX\\nCD\\n1\\nCO\\nI\\no\\no\\nCD\\nO\\n3 _\\nc\\n.o\\n4-\u00c2\u00bb\\n3\\nJD\\nE\\n0 O\\nTo\\nc\\nB\\nc\\nCO\\nc\\no\\nCO CO\\nc c\\no o\\n3 3 3\\nCO\\nc\\nCD\\nCO\\nCD\\nDC\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094 1\\nQ.\\n0\\nO\\nX\\nUJ\\nco\\nSi\\nO cn\\nSi\\nO c\\no o\\nSi\\nCO CO\\nc _c\\nTo\\no o\\n1_ k_\\nCD 0\\nE E\\nX\\nE\\no\\nO\\n0\\n3\\n*0\\no CD\\no !P x\\n-r cc) i\\ng o O\\na\\no o\\n1\\nS a\\n0\\nDC\\nAppendix A National Emissions (1970 to 1998) A-29", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0229.jp2"}, "230": {"fulltext": "Table A-6 (continued)\\nNational Air Pollutant Emission Trends, 1900-1998\\noj cm co CM f.\\nP T-\\nO O CO c\\\\| ifl (O\\nT- CM\\nCOCMCOCOOcO Oi-OjCQ TlO^W\\nt- If) t\u00e2\u0080\u0094 1\u00e2\u0080\u0094 T~ T\u00e2\u0080\u0094 00 CM\\no* CO CnrfT-sioc\\\\i\\n7 in P cm\\no\\nP\\nnwcooo(o^in\\nr- cm\\nCO CM CO co o co \u00c2\u00ab0\\n7- r. If) 7- 7\u00e2\u0080\u0094 7\u00e2\u0080\u0094\\nCM CO M- CD 3 CM\\nT- P CM\\n00\\nCO xt-\\ncn in t\u00e2\u0080\u0094\\nm oo cm\\nco\\noo\\nCOCMCOOOCOj t\\n1- 00 CM\\nCO\\nCO O) oo CO o m co\\nCO CO 7 7\u00e2\u0080\u0094\\nCo CD Co 1\u00e2\u0080\u0094\\nK CM\\nO CM\\nCO -M- t- 3 r-\\n7 in co cm\\n9\\nCO CO co o o\\nco m co cm\\nT\u00e2\u0080\u0094 CO CM\\nM- CM Jfr O)\\nO) K t~\\nO CD CM CM CO\\n7\u00e2\u0080\u0094 CM 7-\\nCM 00 CO o\\nCO\\nCM\\nCO cm CO\\nco p O O co p\\ncm CD M- CM\\n03\\ncocooococnmoocM\\nCM CM CM\\nXfDfflOOO t^CMn\\n7 00 CO 7 CM 1\\nCMI^COCOCO M-CMIO\\nCM\\noo cm o co O)\\ncm in co\\n^O CcotoooinSnmcoCM\\nt- i\u00e2\u0080\u0094 CM CM\\nM-DpKOrJ-pCMCO\\n0O CO T- CM T\u00e2\u0080\u0094\\ncmnQm-coiocmio\\nP Tf\\nCM\\nCO\\nCM\\nO OO 00 V-\\nm co cm\\nin\\nM 1 M CO\\nooNcoo)0)CMU)con ocoom^\\n1-C31CM CO co CO CM\\nCM Tt- CM CM CO O) O\\nT- 7- If) Tf\\nCM\\nK cm o-\\nP G) O O) P t-\\nt- m co cm\\n0)OOOCOCOOONb I)CMlOCOO)EM OQo tCM^CMOjO)\\n7 7 O) CM co fc co CM 7\u00e2\u0080\u0094 I\u00e2\u0080\u0094\\nM 1 CO CO Co CM M\u00e2\u0080\u0099\\nCO Tt\\nCM\\nCO co O 7- o\\nCM CD M-\\nCM\\ns 2\\nCM f to O O\\nco N\u00c2\u00bb 7\u00e2\u0080\u0094 O) CM CO M\\nt- in co\\n7- co K\\nCM O 7-\\nin n* cm co\\nCM 7-\\ncmcmSocococmio\\n7- JO to\\nCM\\no- K\\nO I s N 7~-\\nco cm\\nCD\\nCO\\no):\\nIS\\nCO o\\nE\\na\\nQ) -C\\nsz O\\no o\\no E\\nC CD\\nCD O)\\nS 6\\nO\\nO\u00e2\u0080\u0099 co\\nO\\nE\\nC3\\no\\nSo\\n03\\nCD\\nE\\nCD\\nc\\nLU\\nuT\\n03\\no\\ncr\\no\\nCO\\n03\\n1_ D\\n7 C\\nO CD\\n0-\\nCD\\no\\nD\\nCD\\no\\nCD\\nE\\nco\\nCD -C\\nCL 0.\\nw\\nc\\nI\\nCD\\nc\\nc/3\\nCD\\nCD\\no\\no\\nCD C5 CL\\ni\\nCO 5\\n3 0\\nE V.\\nIon.\\nQ Oc 2 CD\\nZ. 0- a5 8 .2\\nl co\\n\u00c2\u00abJ o\\n\u00c2\u00b0S Z\\n5\\n03\\nc\\n\u00e2\u0080\u0098CD\\nCD\\n0\\no\\no\\nqI\\n_CD\\nas\\n03\\nV,\\nCD\\nS\\no 03 E U\\n.C S C\\nN O q CX cd\\nk_\\nCD\\nUJ\\nPE\\ni\\nO Q\\nCD T\\nH\\nCD lu\\nCD nr\\nCD\\nC/)\\nCD\\nL.\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094\\nCO\\n3\\n\u00e2\u0096\u00a0O\\n_c\\n~o\\nd\\ncc\\n\u00c2\u00a9a\\no\\nO Q)\\n3 c\\n8 I Ql\\n03 s O\\nm Elj\\n-J\\n03 O\\nUj\\nQ.\\nCD 03\\n=s 2\\n1\\n2\\n03\\nc\\n\u00e2\u0080\u00a25\\no\\n5\\no\\n.o\\ns\\n2\\nCD\\n13 v.\\nO 03\\np\\nUj\\nCO\\np\\n8\\n03 O\\nQc\\n5 0-\\no\\n\u00e2\u0080\u009c5\\nc\\no\\no\\n\u00e2\u0080\u00a2O\\no\\nO\\n03\\no\\nD\\n\u00e2\u0096\u00a0O\\no\\nQl\\no\\no\\n\u00e2\u0096\u00a0O\\no\\n3\u00e2\u0080\u0094\\nCL\\nO)\\nc\\n1c\\n(I)\\n\\\\u\\ne\\nCD\\nCD\\ns\\nS3\\n\u00c2\u00b11 Q\\nwpc\\niy\\ns\\no\\n5 .03 -3} c\\nn eg\\nas \u00e2\u0080\u00a2p .5 E 3\\n3^ c 73 p 5\\no\\nI S S3 s\\n03\\n-S2\\nE\\n.c\\n5\\n03\\n03 03\\n-C JC\\n2\\nCD\\nQ.\\nQ.\\n\u00c2\u00b08\\n03\\n03\\no _03\\nV\\nfi\\nJD\\nn\\n0. c\\noQ 5.\\n03 Q.\\nro S\\no. 2\\n\u00c2\u00b03\\n_Q. 03\\n\u00e2\u0096\u00a0o CD O\\no\\no\\nA-30 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0230.jp2"}, "231": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\n\u00e2\u0080\u00a2a\\nD\\n3\\nC\\nMB\\n4-\\nc\\no\\nO\\nto\\nI\\n0)\\nn\\n(0\\n00 r CO y\u00e2\u0080\u0094\\n^OOt-O-^tOOO\\nN o o o o\\nC*5\\nOOOOQOOQO\\nn c\\\\j\\nNNOiooiftinooon fio\\n00 CQ T-\\no o o o\\n00\\no o o o\\nooooooooo\\nCO c\\\\|\\nCM CO OO CO O)\\n00\\nOCOOOOCO OOT-O t\\nooor~oooo\\n00\\no o o\\n0 0)000\\n2SS to iP2 no oo(o oooo\\nCO 0O C\\\\j Co T-\\n_ SNOOOOOOOOt-C\\\\|CDQOo\\n7 7 c\\\\|\\nCOCOOOKcpCOcOOOOCDCOOOO-M-\\nCO 00 CM CO\\nOOOOOOOOOOt-COCOOOo\\n2 2^ T cm\\nCOCDCONCOCMcOOOOLO OOOOTt\\nco oo cm co t-\\nCO\\nZ Z\\nO O O O O O Tt\\n00\\nCO\\n0^0\\n2\\ncomONco -cooi-\\nCO CO CM CO\\nO O CO O O O M-\\ns\\n2 Z\\nOOOOOOCOCMCOOOO\\nTt f- CO\\nCO\\nO co 00 Q co\\nO- CM CO\\no CO n O O O CO\\nCM o\\n-7 -7\\no o o o o o\\no\\nCM\\nQ O o\\nCO\\nM- M- CO M- CO\\nTt CO CM CO\\nO CO O O O CO\\n\u00c2\u00a3MOOOOOOOOt-\\n-7\\nCO 03 O T o\\nt- cm\\ntJ\\nu\\n3\\nc\\nc\\no\\nC\u00c2\u00a3\\njeo\\nUj\\n0\\nJO\\nUj\\no\\no\\ncc\\no\\n3\\n\u00e2\u0096\u00a0O\\n2\\nCL\\no\\nCO\\nCC\\n-J\\n3\\ns\\n:3\\nI\\n1\\nCO\\n3\\no\\na\\nc\\nCC\\n1\\nO O\\n13\\n2 o\\n03 CL\\n2\\ng I\\ntr\\nc\\nE E\\no\\n.c\\nCO\\nCO\\nCO c 5\\nif)\\n0\\nif)\\nif)\\n0\\no\\no\\ne\\ncc\\n3\\nCr\\nw\\nc\\n2 2\\nO W co O\\nE t\\n3\\n\u00e2\u0096\u00a0D .9-\\nO 3\\nJr cr\\nCL LU\\n.2\\nc\\n9 o\\n_c\\nO O\\nco a)\\n2\\nc\\nCD\\nE\\ng.\\n3\\ncr\\nLU\\nc\\nO c\\n.2\\nt ts\\nS\\n3-\\n\u00e2\u0080\u009c2 co\\nS c\\n2 o\\nt- o\\nCO\\nk\u00e2\u0080\u0094\\nto\\n3\\nO\\nc\\n3\\no\\n0\\nc\\n0\\n0\\no\\nif)\\n2\\no\\np\\n\u00e2\u0080\u0094J\\np\\n3\\nK\\n2\\ns\\no\\nCO\\nCO\\nco tr\\nCO .2\\n2 a. O\\ns\\nCO\\nc\\nJ?\\no\\no\\nCC\\n\u00e2\u0080\u0099l_\\n0\\n3\\n\u00e2\u0096\u00a0D\\nc\\nc\\n*c\\n0\\no 5 C\\n0\\nQOQWO\\no\\nI\\nI\\nc\\no\\nCC\\nN\\n1 S3\\nw\\ns\\ntr\\nD o\\no 9-\\nCO\\nO 2\\nCO t-\\no o\\n3 3\\n-O TJ\\no o\\nk_ k_\\nCL CL\\nE E\\n3 3\\n_\u00c2\u00a9\\no o\\n1 _ L_\\nCL CL\\nofl 08\\nE E\\n3 3\\n2 2\\nCL CL\\ntr\\no\\n0\\no\\nCO\\nQ.\\no\\nCL\\nCC\\n0\\n0\\nL_\\nif)\\nC\\nk_\\no\\nC\\nCO\\nO)\\n0\\nO\\n0\\ni\u00e2\u0080\u0094\\nCO\\nI-\\n1\\n0)\\nCO\\n0\\nH\\n0\\nTo\\no\\ncc\\no\\nk_\\no\\nU)\\nc\\no\\nO\\nE\\nE\\nco\\no\\nE\\nE\\n0\\n0\\nt:\\nsz\\n0\\nn\\nJ=\\nO O\\ni_\\nCO\\no\\no\\nO\\no\\n0\\no\\no\\n\u00e2\u0080\u0098c\\n\u00e2\u0080\u0098c\\no\\n*c\\nc\\n0\\n0\\n5\\n0\\n0\\nO)\\nL_\\n0\\nCD\\ni\u00e2\u0080\u0094\\nCD\\nL_\\no\\nO)\\nL-\\no\\nJjC\\n3\\nco O O\\nc\\njC\\nCD\\nc co-af\\n10\\nT3\\na I\\n8 t\\ncc o\\no\\ntr\\no\\nQ.\\nw\\nc\\nCC\\nl\u00e2\u0080\u0094\\nH\\nw\\n.2\\nl_\\ncC\\n3\\nm\\nAppendix A National Emissions (1970 to 1998) A-31", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0231.jp2"}, "232": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nT3\\nD\\n3\\nC\\n\u00e2\u0096\u00a03\\nC\\no\\nCO\\nI\\n0\\nJQ\\nCC\\nco cd o in oo k\\n05 CD tJ- CD CO K\\n05 C\\\\|\\n(flctino fl(o\u00c2\u00aeoooo\\nO)0lTtC0\u00e2\u0080\u0099 C0K\u00c2\u00bb\\noi cm t- t-\\nco to o o O\\nCl C5 O) K\\nC\\\\| 1\u00e2\u0080\u0094\\nO O O C\\\\J T-\\nK CO CM o ID CO\\nO) CO CD CM r\\nCO -M- Os. cm CO CD Tt\\nCD CM T~ -M-\\nT- T~ rt\\nCD\\nO O O cm\\nO O\\n00\\nCM\\nO O O CM\\ncm\\nCM C\\\\j O\\nCD CD\\nID\\nCM\\nto N O C\\\\| (O M-\\n\u00e2\u0096\u00a0M- M- T~ M-\\n7- 7 fr\\nCD 0 0C\\\\|000\\n00\\nCM\\nCM\\nCM CM O ID\\nCM CD CD CM\\nCM\\n(ONOlCMtOOiOCD\\ncn M- rr \u00e2\u0080\u00a2m-\\n7-7- rj-\\nO CM O O O 00\\nCM\\nKo\u00e2\u0080\u0099~coir^co-^ooooo\u00e2\u0080\u0099 cocooo\\nLO tD Ol CO CD CD CD CM\\nCM i- cm\\n0)(00) 0|KOmCD\\nCD CO Q sfr\\nt- t- D-\\nO CM O O O\\n2\\nCM\\nr* CD t- CM CD \u00e2\u0096\u00a0M- CM\\nN CD M D CO\\nCM -i\u00e2\u0080\u0094 7\\no o o\\nCo CD CO O\\nCo CD CD\\nCM\\nCD\\nCM\\nCM\\nis. o CM CM K tj-\\n05 00 CM\\nt-\\nCD7-.ot~OCMOOC\\n2 P\\nCM\\n00 CD r- CM CD CD\\nCo O) CD CO 05 00\\nCM 7- 7\u00e2\u0080\u0094\\no o o\\nO K CO CO Q O CO\\nCp CD CD CM\\nCM\\nN CM O\\n05 00\\n-M-\\nCM Tt\\nCD\\nO CM O O O 00\\nCM\\n05 CD C5 (O CM\\nCD M- CD 05 00\\nCM 7\u00e2\u0080\u00947-\\no o o\\no 2 oo Ns o\\n00 CD CD\\nCM\\n05\\nCOCDCOCM00CDCDCD\\n7- C5 CD Tt\\nCM CM CJ-\\nO O O CM\\nO O O K\\nCM\\n5\\nCp Tf\\nCM\\nCo oo O 05\\nCM 05 N\\nOOOOOCOOOCOO\\noo CD CD\\nCM\\nCM\\nCD\\n7- CM\\nCM\\nCM CM\\n00 CM CD CD\\nCD\\ndOOCMOClO\\nK\\nCM\\nJCONtJlNKOOOOOOiON^OClOOlSCMCD\\nCD M CM CO K rs CD CD 7\u00e2\u0080\u0094 t\u00e2\u0080\u0094 7\u00e2\u0080\u0094 C5\\nCM 7\u00e2\u0080\u0094 CM CM CM\\n00 Cm CD CM\\nO O C5 T~\\nO O O K\\nCM\\n0\\n-I\\na\\nQC\\n-j\\n0\\no\\n0\\nVi\\nQ\\nIS\\nVi\\nI\\n\u00e2\u0080\u00a2S\\ng| s\\n.3 Q)\\nCO\\na?\\nCD\\nO)\\nJ\\nO c\\nQ5\\nQ.\\no\\nI is\\nep\\na o\\no\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094I\\n03\\n1\\nCO\\n03\\n.03\\nu\\nV)\\n3\\nO\\nc\\nLL\\nO\\nc n\\nJO\\nTD\\nC\\n03\\nCD\\nJO\\nUJ\\n-J\\no\\nI\\nQ\\no\\nCC\\nO\\nn\\n05\\nO\\ns\\no\\nk_\\no\\no\\noS\\nC/5\\n0\\nO\\n!n\\n05\\nw\\nro\\n0\\n3\\nQ\\nc\\n7 o\\nCO\\no\\nfa\\no O\\n7 CM\\n25 J5\\n05\\n05\\nC/5\\n05\\nO\\n!c\\nCD\\nC/5\\nO\\n0\\no\\n9 2\\n05\\n25\\n05 .9:\\nX Q\\n73 as\\np 5 5\\n-C -2\\n0\\nUj\\n-J\\no\\n5\\nQ\\n0\\nUj\\nS\\n0\\nS\\nQ\\nO\\nCC\\n3\\no\\n2\\n05\\nC\\no\\nm\\n05\\n0\\n\u00e2\u0096\u00a0o\\nCO\\no\\nCC\\nI\\nc\\no\\nc\\n.0\\nO m\\n5 -S\\nto\\n8\\n0 S\\nc\\nI\\nCO\\n05\\ni\\n-2\\n.03\\n05\\nE\\n1\\no\\n-2\\n05\\nw\\ne/5\\na\\n05\\nO 05\\nS\\n2 c\\nC 03\\n05 05 C\\n\u00e2\u0096\u00a02 .c -8\\n03 2\\n05 P\\n_ 03 -2\\nO) is 3\\n1\\nis -i 5 I a\\n05\\nC5l J\\nA-32 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0232.jp2"}, "233": {"fulltext": "Table A-6 (continued)\\nNational Air Pollutant Emission Trends, 1900-1998\\nis\\nis\\ncm\\n00 00 CD Op Op Is\\nCO Co CO\\nCM h- 03\\nCM CO\\nK o o in\\nCO CM\\nT- O\\n03 03\\nK\\n03\\nCM CM\\nCM\\nCO\\n30\\nco\\n03\\n\u00e2\u0096\u00a0D-\\nCD\\nIs\\n03 00\\n0\\nCO\\n10\\nco\\nrs\\nCO\\nto\\nCD\\n00\\n00\\nr^*\\nCO\\n03\\nT\u00e2\u0080\u0094\\nCO\\n03\\nt\\nCD\\n00\\nUP\\n|s\\nCM\\nCO IS CO If) Co Is\\nCo Co t- CO s-\\nCm I CO\\nCM CO\\no o\\nCO\\nin\\nCM\\nCM\\nD\\n0\\nO CM\\ncn\\nUP\\nIs\\nCO\\n10\\n\u00e2\u0096\u00a0X\\nfs\\n03\\nLO\\nCD\\n03\\nCD\\nup\\nup\\nCO\\nco\\n03\\nco\\nUP\\nco\\nCO\\nCO\\nr-\u00c2\u00bb\\nlo\\nco\\n00\\nM-\\nrs\\nCM\\nCo CO CM CO Co IS\\nCD CD CO\\nC\\\\l 00 00\\nCM CO\\nCO O O Tt\\nCO CM\\nco\\nCO\\nCM\\nCO\\nIs\\n0\\nCM D-\\n03\\n00\\n0\\nis\\n03\\nC3\\nUP\\nCO\\n00\\nD-\\nO\\nT\u00c2\u00bb-\\n03\\nCD\\nD\\nis\\ncm\\nup\\n03\\n00\\no_\\nCD\\nco\\nCO\\nup\\nIs\\nT\u00e2\u0080\u0094\\nCO\\nCM\\n(s\\nCM\\ncl- CO\\nCO CO\\nIS. CO Co\\nCO\\nCO T-\\nCM CO\\nCMO O\\nCM\\nO\\nIs |-m\\nup\\nCVJ\\nIS\\nup\\n\u00e2\u0080\u00a2D t\u00e2\u0080\u0094\\n00\\n03\\nU3\\nK\\nK\\n03\\npm\\nIT)\\nCO\\n00\\nCD\\nCD\\nup\\nX\\nrs\\nIs\\nD-\\n(D\\n00\\nIs\\nO\\nco\\nup\\nT\u00e2\u0080\u0094\\nup\\nK\\nis\\nCM\\nrs\\nCM\\nM-\\nup\\nCO CVJ co\\nT- 1- OP\\nCVJ\\nY~ D- CO\\nO CD T-\\ncp J\\n-D\\nO\\nT\u00e2\u0080\u0094\\nCO\\nup\\nCD\\nO CO\\n03\\nD-\\n03\\nCD\\nUP\\nCD\\nCD\\nCO T\\nCM\\nCO\\nCM\\nCM\\nCM\\nCO\\nup\\n00\\nO\\nQ\\nCD\\nD-\\nT\u00e2\u0080\u0094\\nrs\\nCD\\nCD\\nCD\\nG)\\n00\\n03\\nUP\\nIS\\nCO\\nCO\\nT\u00e2\u0080\u0094\\n03\\nup\\nco\\nTs.\\nis\\nCO\\nis\\nCM\\nU) UP C3 03 CM 00\\nCO CO CO\\nO\\nCO CO\\n\u00e2\u0080\u00a2cj- CO\\nCM\\nO CO\\nM\\nK\\nco\\nf^.\\nCD\\nM-\\nCD\\nO CO\\nCO\\nco\\n0\\nY\u00e2\u0080\u0094\\nIS\\nCM\\nCO\\n0\\n00\\n03\\nD\\nT-s\\nCD\\nco\\nCM\\n03\\nCO\\nCO\\nCO\\nCD\\nK\\nco\\n03\\nCD\\nvf\\nCD\\nT-.\\nrs\\nco\\n|s\\nCM\\nco M- op cp\\nco co Is\\no\\nCM CO\\nCO CO\\nIf) co o o\\nCM CO\\nCP D-\\nD-\\nCO\\nop\\nCO 0 CD\\nCM\\nCO\\nop\\nCO\\nUP\\nIS\\n03\\nco\\nCO T\u00e2\u0080\u0094\\nD-\\n0\\nOP\\nop\\nCO\\nCO\\n03\\n00\\nCO CM\\ncd\\nCO\\nco\\n00\\nCO\\nrs\\nCM\\nCO M- 00\\nCO CO\\ny- M-\\nCO CO\\nCO co O CO\\nCM M-\\n1- O cm CM\\nCo CO\\nD-\\na\\nIS\\nCD\\n0 co\\nD-\\n0\\nCO\\n50\\n03\\nQ\\nCD\\nCO\\nO\\nIS\\nX\\n0\\nT\u00e2\u0080\u0094\\nCD\\nCO\\n0\\nOP\\nCO\\nCO\\nCO\\n00\\nis\\nIQ*\\nT-\u00e2\u0080\u009c\\nco\\nis\\nIS\\n|s\\nCM\\nK If) 00\\nco co Is\\nCM\\nT- CM\\nCO CO\\nIO CO O CO\\nCM M-\\nD-\\nTt\\nD-\\n03\\nCM\\nfs O\\nCO\\nIS\\nF J\\n0\\nIs\\n00\\n4m\\nop\\nCO\\ns\\n00\\nCD\\nCO\\n00\\nco\\niG\\nco\\nup\\nCO\\nCM\\n0\\n03\\nO\\ncq\\nup\\n00\\n03\\nup\\nT-\u00e2\u0080\u009c\\n4-\\nCD*\\nis\\nO\\n0)\\n3\\n.c\\nc\\no\\nu_\\nVi\\nUJ\\n-J\\nCJ\\n5\\ns\\nQ\\nVi\\nUJ\\n2:\\n3\\n2\\nUJ\\nQ\\nO\\nDC\\nI\\n2:\\nO\\n2\\nT3\\no\\nDC\\nc\\no\\nco o\\nC C:\\nO o D\\nO 0-\\n2 \u00c2\u00ab0\\nII\\nCO\\nc\\nc\\nI\\n03\\n03\\ni\\nJTJ\\n9\\n0)\\nE\\nE\\no\\no\\nJO\\n0)\\nCO\\nCO\\n03\\n03\\nCJ 03\\nc c\\nCP C\\nf CP\\na 5\\na s\\nc* t\\nIM s\\njp 5 5\\nra\\n03\\njo\\n03\\nCO\\nCO\\n03\\nC 33\\n5 C\\no\\n03\\n\u00c2\u00abP .C\\n\u00e2\u0096\u00a0Q O\\nCO\\na\\nO)\\nE\\n3\\n03\\n03 03\\nQ-\\nO 73\\n03\\nTP\\n03 -Q q O Jtt\\nto co w TP 3\\no 2 2 S. CP /r -5\\nO 3 C O) o D- -5\\nO) o\\nc\\nCO o\\nDC Z\\nco\\nco\\n03\\na\\n3\\nI g\\nCO nr\\ng-o\\n\u00c2\u00a72\\n2\\n2\\nc\\no\\nc/3\\no\\nI_\\n03\\n-O\\nSQ\\nO\\no [y\\nc\\n03\\n03 _J\\nO .J\\nUj\\no o\\nVi\\nco P\\no\\na\\n08 3\\n8\\no c\\n3 co\\no\\n\u00e2\u0080\u0098C\\n03\\n-PC\\no\\no\\n4m\\nCO\\n03\\n5: c\\no\\nco ts\\nc CO\\n3 3\\na= xp\\no F\\n\u00e2\u0096\u00a0g o\\n0)0\\nCP\\n03\\nJO\\n03 *r O\\n5 3 E\\nO)\\nc\\ng co\\no 3\\nO UL\\nCj\\nCP 0 c\\n-2\\n2\\n\u00e2\u0096\u00a0Q\\ncp 03 co\\nQ. i C\\nC co O\\n3 Q. O\\nCO\\ng\\n*k_\\no\\n03\\no\\no\\n03\\nO\\nk_\\n3\\no\\nCO\\no\\no\\n9\\nQ.\\n0\\nCvJ\\nr^\\no\\nCD\\nTD\\nCO\\no\\no\\nco\\n*5\\n3\\no\\no\\n03\\n03\\nJD\\no\\nc\\n32\\nD\\nO\\no\\n03\\nr\\nCO\\nc\\no\\nCO\\nCO\\n3\\n-Q\\nCO\\n0)\\n_D\\n03\\nD\\nO\\n-Q\\n03\\n0\\nQ.\\n3\\nE\\nco\\nc\\no\\no\\nu\\n03\\nE\\nTJ\\niJ C\\nCO CO\\n03 CO\\n3\\nII\\nO\\nCO\\nE\\nCO\\no\\nE\\nU3 03\\nc c o\\nco\\nig r co\\nc c\\nn W o\\nCO\\nCO\\nE\\n03 CO\\nCO .t\\nc E\\n03 03\\nCO\\nQ.\\n03 C\\nO\\nCO o\\no\\nCO\\n-O\\nCO\\n03\\nO\\nCP S\u00e2\u0080\u0099\\nffi\\nC\u00c2\u00b0 co\\no.\u00c2\u00b0\\nc -u\\nII\\nX\\n\u00e2\u0096\u00a0IE\\no\\n5\\nsi\\n0\\nN S\\n0\\n_c\\no\\nO)\\n0\\n0\\no\\n0\\no\\nk\u00e2\u0080\u0094\\n3\\no\\nCO\\n!c\\nE\\no\\nk_\\n0\\nC\\ng\\n\u00e2\u0080\u00990\\n0\\nE\\nw\\nco\\nE\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094\u00e2\u0080\u00a2\\n0\\n0\\n0\\n3\\nC\\nC\\n0\\n0\\nk\u00e2\u0080\u0094\\nQ-\\nk_\\n0\\nC\\n2 S\\nso o\\n3 \u00e2\u0080\u0099(O\\ng w\\nis e\\nD\\nS\\n\u00c2\u00a92\\no\\n\u00e2\u0096\u00a0c\\no\\nx:\\nW 03\\nco\\n03\\nCO\\nl!\\nII\\nw w\\n03\\nc\\n-O 03\\n2 o\\ng 0\\nc k_\\n3\\nk_ 0\\n0 c\\n0 O\\n.Is\\nco co\\n5.\\nE\\n03\\nc\\no .S 5\\nw x:\\nO 03\\n03\\n2 o\\nc\\n03\\ng\\n5\\no\\nx:\\nro\\nc\\n5 2\\no\\nx: o c\\no\\n_ o\\n2 jjj\\n1\\ncop\\nQ3 Cf3\\nE S\\n0 O\\n0\\n0\\nC\\n0\\nc\\n0\\n0\\n0 CO O)\\nxr c d\\n0\\n-o\\nif) C 5\\n|s Q3\\n3\\no -a co\\nc\\n3 n\\n2 8\\nc\\n3 ni -3\\nO H\\nC\\n3\\n\u00e2\u0080\u00a2s E\\nW _j;\\nQ\\na\\nc\\nw S\\ncc 5\\nt X3\\n03\\nw .t:\\nw\\nQ a\\no\\n-o\\no\\nQ. o\\n2 E\\nco 5\\no o\\n0\\n0\\nc\\no\\no\\n0\\nCL\\nE\\n0\\n0\\no\\n0\\nt:\\n3\\n0\\n0\\ng\\nr\\n0\\n~o\\nc\\n0\\n~S\\nc\\no\\nN\\nCvJ\\nr*\\nE\\n0\\no g-\\nO o\\nc\\n0\\nk\u00e2\u0080\u0094\\n0\\n2 E\\n0 0\\nE 2\\no\\n3 $2\\no\\n2 E\\nQ_\\no\u00c2\u00a3\\nV)\\nc\\nO)\\n\u00e2\u0096\u00a0O\\n03\\no\\nE\\no\\nk_\\nO 5\\nc\\nS 7\\n9\\n03_\\nx: 3\\n33 03\\nII\\nr e\\nE 1\\nO\\nx:\\n0\\n0 0\\n0 -n\\n11\\no\\n0\\nAppendix A National Emissions (1970 to 1998) A-33", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0233.jp2"}, "234": {"fulltext": "Table A-7. Lead Emissions\\n(short tons)\\nNational Air Pollutant Emission Trends, 1900-1998\\n00\\nJO\\ny\\njo\\nco\\nCO\\ny\\nY\\nca\\n05\\nCO\\n05\\nCO\\nID\\nCO\\no\\nco\\nU5\\nco\\nY^\u00c2\u00bb\\neg\\nY\\nY*\u00c2\u00bb\\nca\\nO\\nCD\\nJO\\nin\\nCT5\\no\\nCO\\nco\\nY\u00e2\u0080\u0094\\nT^\\nY\u00e2\u0080\u0094\\no\\nK\\nr-\\nK\\n05\\n\u00e2\u0096\u00a0o-\\nY\\nY\u00e2\u0080\u0094\\ny\\nT\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\nl^\\nY\\ny\\nco\\nCO\\nCO\\no\\nca\\nca\\nco\\n05\\nco\\nY-.\\nCVJ\\neg\\nY-\\nco\\nCO\\nco\\nY\\nY\u00e2\u0080\u0094\\nCVJ\\neg\\nY\u00e2\u0080\u0094\\nea\\nO\\nCD\\n00\\nCO\\nCO\\nJ)\\nCO\\nCO\\nco\\nY~\\ny\u00e2\u0080\u0094\\nY\u00c2\u00bb\\no\\n00\\n00\\nco\\no\\nY\\nY\u00e2\u0080\u0094\\nT-\\nY\u00e2\u0080\u0094\\nT_\\nCO\\n1\u00e2\u0080\u0094\\nCO\\neg\\nCO\\nlO\\nCO\\nco\\nca\\nCO\\nCO\\n05\\nCO\\nY*\u00e2\u0080\u0094\\nCO\\neg\\nY\u00e2\u0080\u0094\\nco\\nLO\\nco\\nY-.\\nY\u00e2\u0080\u0094\\nCO\\neg\\nY-\u00c2\u00bb\\ny;\\no\\nN.\\ne~\\nK\\n05\\nCo\\nCO\\nco\\nY\u00e2\u0080\u0094-\\nY\u00e2\u0080\u0094\\no\\nCO\\nCD\\nCO\\nO)\\n\u00e2\u0096\u00a0Y\\nY\\nY~\\nY\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nT\\nCO\\nK\\no\\nca\\nco\\nCO\\nix\\ntx\\nca\\nCO\\nca\\nCO\\nY*\u00c2\u00ab.\\nco\\nY-.\\nCO\\nY\\neg\\nY-\u00e2\u0080\u0094\\nY-\\nCO\\neg\\nY^\u00c2\u00bb\\n\u00e2\u0080\u00a2Y\\nO\\n00\\nCp\\nCO\\ncp\\nO)\\nlo\\nCO\\nco\\ny\\n1\u00e2\u0080\u0094-\\nY-\\nO\\nCO\\nCD\\nCO\\n05\\nY\\nY\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094\\nY\\neg\\no\\no\\nco\\nCO\\neg\\neg\\nca\\n05\\nca\\nCO\\nY-.\\nLO\\ny\\nY*\u00c2\u00bb\\nCo\\nCO\\neg\\nY-\u00c2\u00bb\\no\\nco\\nY-^\\ny:\\nO\\noo\\nCO\\nCD\\nCO\\n05\\nCo\\nCO\\nco\\nT\u00e2\u0080\u0094\\ni\\nt\u00e2\u0080\u0094\\ni\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nO\\n05\\n05\\n05\\n05\\nY\\nY\u00e2\u0080\u0094\\n00\\nJM\\no\\nca\\nCo\\nCO\\neg\\nC\\\\J\\nca\\n05\\nTf\\nca\\nCO\\nY\u00e2\u0080\u0094\\nin\\ny\\nY-\u00c2\u00bb\\nCo\\nY\\neg\\nY~-\\nY\u00e2\u0080\u0094\\nT\\nCO\\nY*\u00c2\u00bb\\ny:\\nO\\n00\\neg\\neg\\nSJ\\n05\\nCO\\nCO\\nco\\nY--\\nt\\nr~\\nY~\\nO\\n05\\n05\\n05\\n05\\n\u00e2\u0096\u00a0o-\\nY\\nT\u00e2\u0080\u0094\\neg\\np5\\nco\\nY\\nY\\neg\\neg\\nca\\nCO\\nca\\nco\\nY\u00e2\u0080\u0094\\nco\\nY\u00e2\u0080\u0094\\nY\\nY\\neg\\nY\u00c2\u00bb\u00c2\u00bb\\no\\nco\\nY\u00e2\u0080\u0094\\n\u00e2\u0080\u00a2Y\\nO\\nN-\\nS3\\nco\\nS3\\n05\\nlo\\ny\\neg\\n1\u00e2\u0080\u0094\\ni\u00e2\u0080\u0094\\ny\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nT\u00e2\u0080\u0094\\nY-\\nO\\n05\\n05\\n05\\n05\\n\u00e2\u0096\u00a0o-\\nY\\nr\\ny\u00e2\u0080\u0094\\nco\\nco\\nXL\\nY\\nCO\\nCQ\\nca\\nCO\\nLO\\nca\\nCO\\nY~-\\nco\\neg\\nY~y\\nCO\\nCO\\neg\\nY**.\\no\\nco\\nY\u00c2\u00bb\u00c2\u00bb\\nY\\nO\\n05\\neg\\neg\\nS3\\n05\\nco\\ny\\neg\\ny-~\\ny^\\nY~\\nY\u00e2\u0080\u0094\\nO\\nco\\nco\\nCO\\n05\\nY\\nY\\nY\u00e2\u0080\u0094\\nY\\nT\\no\\nY\\nCO\\nco\\nY\\nY\\nco\\nCO\\nca\\nCO\\nca\\nCO\\nY-~\\nco\\nco\\nY\u00e2\u0080\u0094\\n00\\nY\\nco\\nY\u00e2\u0080\u0094\\no\\nco\\nY^\\nY\\nO\\nO\\nCO\\nco\\nCO\\n05\\nCO\\nY\\neg\\nv\u00e2\u0080\u0094\\ni\u00e2\u0080\u0094\\nY~\\nY~\\nt\u00e2\u0080\u0094\\nY^\\nO\\nCO\\nco\\nCO\\n05\\nY\\nY\\nY\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\n05\\nlx\\nCO\\n2P\\nY\\nY\\nca\\nCO\\nQ\\nco\\nY^\\nco\\nY\u00e2\u0080\u0094\\nca\\nY\\nco\\nY\u00e2\u0080\u0094\\nY^\\n*vj-\\nco\\nY\u00e2\u0080\u0094\\nY\\nO\\neg\\nco\\nCD\\nCO\\nCO\\nCO\\nY\\neg\\ni\u00e2\u0080\u0094\\nc\\\\j\\neg\\nY-\\ny\\nSi!\\nO\\nCO\\nco\\nCO\\n05\\nY\\nY\u00e2\u0080\u0094\\nY\\nY\u00e2\u0080\u0094-\\n00\\n1\u00c2\u00b0\\nCO\\noo\\nY\\nY\\no\\nO\\nca\\n05\\nca\\nCO\\nY~~\\nm\\nco\\nY^\\nCO\\nin\\nco\\nY~-\\nY~-\\nin\\nY\\nY~~\\nY\\nO\\nCD\\nCO\\nCD\\nCO\\nco\\nco\\nY\\neg\\nY^\\neg\\neg\\nY^.\\nSi!\\nO\\nCO\\nCO\\nCO\\n05\\nY\\nY\\nY\u00e2\u0080\u0094\\nYyy\\nY\\nCO\\nY\\nco\\nCO\\nco\\nco\\nca\\no\\nC\\\\J\\nco\\nco\\neg\\n00\\nK\\nt\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\\nCD\\nY\\nY\u00e2\u0080\u0094.\\nY\u00e2\u0080\u0094\u00c2\u00bb\\nco\\nY*\u00c2\u00bb\\nY\\nO\\nCO\\n00\\n00\\noo\\nCO\\nCO\\nco\\nY^\\ni\u00e2\u0080\u0094\\nCO\\nCVJ\\ny\\neg\\nO\\n-i\u00e2\u0080\u0094\\nY\\nY\u00e2\u0080\u0094\\n05\\nY\\nY\\nY^\\nY\u00e2\u0080\u0094\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nr\u00e2\u0080\u0094\\nO\\n05\\nCO\\nK\\nSP\\n05\\ny\\ny\\nca\\nca\\nLD\\ni\u00e2\u0080\u0094\\nca\\nY\\nY\\nY\u00e2\u0080\u0094\\nY~\\neg\\nco\\neg\\no\\n05\\nY^\\nY\\nO\\n05\\nY\\nY\\nY\\noo\\neg\\n05\\nlO\\neg\\nco\\nCO\\no\\nCO\\nY-\u00c2\u00bb\\ni\u00e2\u0080\u0094\\nY~\\n00\\nca\\no\\nca\\n05\\nY-\\nY\u00c2\u00bb\\no_\\nY~\\nY-Y\\nY\\nY\\nY\\nco\\no\\n05\\nco\\n05\\n_\\no\\nY~\u00c2\u00bb\\no\\nca\\neg\\nK\\nCD\\nY-\\nSi!\\nCD\\nco\\neg\\nN\\nY\u00e2\u0080\u0094\\nca\\nY^\\nY\\nO\\nCD\\nca\\no\\nca\\nN\\ncp\\n00\\nY~-\\nco\\nV-\\nY\\ny\\nN\\nCD\\ny\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\ni\u00e2\u0080\u0094\\nY-\u00c2\u00bb\\nY\\nT\u00e2\u0080\u0094\\nT\\nO\\neg\\neg\\neg\\n05\\neg\\ni\\nca\\no\\nY*-\\nY\u00e2\u0080\u0094\\nca\\no\\nY\u00c2\u00ab\\no\\nfx\\no\\n05\\nca\\noo\\nlx\\nca\\nrs\\n00\\nco\\nco\\nK\\nCT\\nIX\\nY\u00e2\u0080\u0094\u00e2\u0096\u00a0\\nJM\\nY^\\nTt\\nCO\\nY-~-\\no\\nI\\nco\\nco\\nCO\\nr\u00c2\u00bb\\n05\\nS3\\nco\\no\\nCO\\nco\\nY\u00e2\u0080\u0094\\n00\\nco\\neg\\neg\\ncp\\neg\\nCVJ\\ny\\nY\u00e2\u0080\u0094\\neg\\nY^\\nCo\\nca\\n5\\no\\no\\nY\\nca\\nY-^\\no\\no\\nY\u00e2\u0080\u0094\\n=T o\\ni-\\no\\nUJ\\nUJ\\nCQ\\no\\no\\nUJ\\ng\\nC/5\\na\\no\\nc\\nE\\na\\nCO\\no\\nO\\n3\\nO\\n,C\\n6\\na\\n5\\n-Q\\na\\nw\\n0)\\nc\\nO)\\n3\\n0)\\no\\n2\\nx:\\nc\\nCO\\n-I\\n3\\nI\\nI\\n0\\nCD\\n0)\\nCD\\n1\\na\\no\\nc\\nE\\na\\nI\\nCO\\no\\nO\\nCO\\na\\no\\nc\\nE\\na\\n\u00e2\u0080\u0099\u00e2\u0096\u00a0Q\\n\u00e2\u0096\u00a0o\\na\\nCO\\n05\\nc\\no\\n\u00c2\u00b0S\\nCD\\no\\nc\\nCO\\n1\\nco\\n2\\nQC\\ni*\\nO\\n1 g\\n1 8\\nCO\\nO\\nO\\ncO\\nc\\no\\nCO\\nc\\nla\\no\\n1\u00e2\u0080\u0094\\nCD\\nE\\nE\\no\\nCO\\na\\no\\nc\\nE\\na\\na\\no\\n.c\\n-Q\\n-Q\\na\\nCO\\nCO\\nc\\nCD .2\\n1 .2\\nto\\nc\\nCD S\\nl a\\ns\\nc\\nco\\nCD\\nE\\nE\\no\\no\\n1\\nco\\n2\\nCD\\n1 V.\\ns\\n.CO 5\\n6 o\\nCO\\nc\\nCD\\n\u00e2\u0096\u00a0g\\nco\\nCD\\ncc\\nQ.\\nCD\\no\\nX\\nm\\nJD\\nE\\no\\no\\nCD\\n1\\nh\u00c2\u00bb\\no\\nQ\\no\\nDC\\n0.\\na\\n75 o -S\\nCD\\na\\nLL.\\n6\\nCO\\n.ca\\nc\\nD\\nTD\\nCO\\nCD\\nDC\\n-J\\n08\\n3\\nI\\no\\n05\\nCO\\ng\\nCD\\ng\\nc\\nCO\\nS? .9\\no\\nc\\nCD\\n.1\\nCL\\n\u00e2\u0096\u00a0O\\nc\\nco\\n\u00e2\u0096\u00a0Q\\nCO\\nA-34 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0234.jp2"}, "235": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nco\\nCO\\nT-\\nco\\ncp\\nCO\\nCO\\nCO\\nK\\n1\u00e2\u0080\u0094\\nY-\u00c2\u00bb\\nC\\\\J\\n3\\nY\\n03\\nco\\nco\\nCT)\\nCT)\\nr^-\\nCM\\nCM\\nO\\n00\\nY-.\\nt}-\\nY-x\\nK\\nY\\nCD\\n3\\nn\\nco\\nco\\nY-x\\nLO\\nT\u00e2\u0080\u0094\\nCO\\nevT\\nT\\nfs\\n3\\nO)\\n00\\nY\\nS)\\nK\\nY\\nY-x\\n00\\n0\\n00\\nco\\nCO\\n00\\nCD\\ns\\nCM\\nT^.\\n00\\n00\\n3\\nY\u00c2\u00bb\\nCO\\nY-x\\nCO\\nY\\nCD\\n3\\nn\\nCO\\nY\\n10\\nCO\\nT\u00e2\u0080\u0094\\nCM\\nT\u00e2\u0080\u009c\\nco\\nU)\\nCO\\n00\\nSN\\n00\\nY\\ncp\\nCO\\nCO\\nY\u00e2\u0080\u0094\\nCD\\n3\\n00\\n00\\nO\\nCO\\nO)\\no\\nCO\\nCO\\nCM\\nK\\nO\\nX\\nC\\\\l\\nYx\\nCO\\nY\\nCT)\\n3\\nco_\\nCO\\nco\\nY*x\\nin\\nCO\\nT\\nCM\\nin\\nO)\\nr^-\\nCM\\nCM\\nCO\\nY-x\\nco\\nC 3\\n00\\n03\\nO)\\nCM\\nO)\\n3\\nco\\nN.\\nCM\\nY\u00e2\u0080\u0094\\nco\\nK\\nC 3\\nCM\\nY-x\\nIf)\\nY\\nCT)\\nC 3\\nco\\nCO\\nY\\nY**-\\nto\\nX*\\nCO\\nT\\ncm\\nT_\\nN.\\nD-\\nSN\\nCO\\nY\\nY\\nY-x\\n0\\nO\\nCO\\n00\\nC 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P CD\\nO C o\\nO U\\nJj -2\\neg 5= o\\nTD CD CD\\nC -Q O\\n8 P P 2\\ns \u00c2\u00abX3 eg\\nw -2 -2 o\\n03\\nc\\n0\\n0\\no\\no\\ncl\\ncn\\ns\\n0\\n0\\n3\\no\\nl\u00e2\u0080\u0094\\n0)\\nO)\\n.c\\no\\n-3\\n3\\nC\\nCD\\n8\\nCD\\nJC\\nO\\nO\\nc\\no\\no\\n3\\ntj\\nO\\nc\\no\\na 3\\nO O\\nI 2\\nCT3 Q\\nC\\n8\\nc\\no\\no\\nO\\n8\\na\\n35\\nc\\no cjj\\no\\np\\np\\nc\\np\\nCT)\\nc\\ncd\\nCD\\nCD\\no\\no\\nT Q-\\n5: CD\\nCD 5\\nD)\\nra\\nQ 3\\nO)\\n.c\\n2\\n53\\nCD\\n8\\nCD\\nO\\n0\\nUJ\\nCO\\nCO\\nUJ\\no\\no\\noc\\na.\\n~j\\n2\\nI\\nI\\no\\nCD\\nO\\n3\\np\\nO\\nCO\\nv_\\nCD\\nCD\\n.C\\nC\\n3\\nO\\n2\\n3\\nC\\nCD\\n6\\nc\\nCD\\n8\\nD\\nO\\nCD\\nD\\nCD v 3\\nCD\\ncd x\\no \u00c2\u00abj\\n2 O\\n5 o\\neg m\\nOC\\nCD\\n3\\np\\nc\\nw 0\\nO\\na.\\nco\\nQ\\nla\\nCO\\nI\\nC\\no\\n03\\n0\\nc\\no\\nC\\n0)\\n0\\nCD\\n.Q-\\n.O\\n8\\n3\\n8\\nu]\\nd\\nl\\nQ\\nO\\nOC\\n3\\nO\\nCD\\na\\no\\no\\nk\u00e2\u0080\u0094\\no\\no\\no\\n0\\n0\\nO\\n0\\n0\\n0\\n0\\nO\\n3\\n0\\n0\\nO\\nlc\\n2\\nCD\\nCD CO\\nCO O\\nu o\\n3\\n3 3 Q\\nQ Q 4,\\nr\\n-C -C CO\\nCT) CT) CD\\nX\\nAppendix A National Emissions (1970 to 1998) A-35", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0235.jp2"}, "236": {"fulltext": "A-36 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0236.jp2"}, "237": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nc\\no\\n75\\nw\\ni\u00c2\u00a7|\\no\\no\\n-C\\n1\\nE\\no\\n00\\nI\\n0\\n.O\\n7t CO\\n^OCVJ- frO OO- tOO\\n7* CO\\n-\u00c2\u00abfr CO O CM\\nK o CM\\no^y^ooocn^ooiQM^OLno^ooLn co o\\nCO CD K oo Co CO CO\\nOinPOOOO\u00c2\u00a3D ls C l OOifiO l OOlO oo\\nto CD N. CQ CO CO to\\ntoocMTj-oSio^j-cn-r-tnKocMT-OLncoooor^cvjuoocooLno^OTt coo\\nco to cn k oo co co co\\nOcccoeooTj-cooocoocM\\nC) OCOO^--tOOCOOCMT-\\nm 8 n\\n-7 CO 7 7 7 00\\nID CO CO\\n7 7 7 7 tO\\no otoo t tooeooN 1 ifl2 co\\n-7-7-7 1\u00e2\u0080\u0094 \u00e2\u0080\u009c7 CO -7 \u00e2\u0080\u009c7 \u00e2\u0080\u009c7 CO\\nr- toocoocooco coo\\ncv 77 xj-\\nr- coocoocooco co o\\ntv 9? ^7 Tt 77\\nCOOCOOCOOCO COO\\n\u00c2\u00b00777(OI!^2\\n=i 0 VO 3-COOOOOOC\\\\Ji- ir)CO CO^-r C OOCDOCOOCO COO\\nP; -J -5 t- -5 co-7-?^co r ~K-7 77 o-\\nz z z\\notvo^rcooo\\n-7 -7 -7 7\u00e2\u0080\u0094\\nco O CM\\n0 OlVOTfCOOOCOOCM\\no CO CO\\nz $2 z z z\\nID CO CO\\n\u00e2\u0080\u00a27 to 7 7 7 CD\\nCOOCOOCOOCO COO\\n-7 77 -M O\\nCOOCDOCOOCO CO\\n-7 77 Tt rj-\\nI-\\nJ\\nUj\\n*J\\nUJ\\noci\\n5\\no\\no\\nUj\\nu.\\nCO\\nO O\\nCD\\n(0\\nCD\\n3\\nc ct\\n.2 P\\n3\\n2\\n!1\\no\\n\u00c2\u00abs 5\\nO\\no\\nc\\nUj\\nu.\\n.2\\nc\\ncd\\nCD\\nCO CD\\no ffl c\\nOO0-\\nT8 ffl\\nC C C O\\no o o x\\nc\\n0 3 3\\ntD Lu\\n3\\n.Q\\nE\\no\\no\\nUJ\\nco: .Q cl)\\n5\\no\\nori\\nC/) CO CO\\nc c c\\nE 5\\nb o O\\nCO CO CO\\no o p\\no r\\nCO\\nQ)\\n-C\\nCD CD CD\\nE E E\\nE E E\\no o\\nCD\\n3\\no\\nO\\n-jOO0 O\u00c2\u00a3-lOOO\\nUj\\ng\\no\\no -j=\\n3 E\\n\u00c2\u00b0e\\nCD\\nO)\\nS O)\\n_\\n_ ro S\\nCO 0\\no c\\nP fc CD\\n_ Q) CD\\ncd -c cc\\nSS-\\nC 0)\\nCO E\\n10 pi t\\nCD o\\n1 o\\no 0\\nJD\\nCO\\np\\nE\\n0)\\nx:\\no\\ncO\\nk-\\n3\\n3\\np\\n*k_\\nCD\\n6\\nCO\\nSi\\n1\\n5\\n5\\n5\\n3\\n5\\no\\nE\\nCD\\nc\\ncd\\nCD\\nCD\\no CD\\nCD\\nc\\nE\\nCO O\\nCD O\\ni\\nCO\\nUj\\no\\no\\nc\\n0.\\n12\\nD 5\\no\\nL_\\nCL\\nw t:\\nCO 0.\\nQ) CD\\nS s\\no\\nL_\\nk\u00e2\u0080\u0094\\n0)\\nc\\no\\n0\\nuj\\n2\\nI\\n0 s\\nD) -cr\\nH\\ncd Uj\\nCD\\nCD\\nO s\\ni\\nTO\\nCD\\n_co\\nCD\\nDC\\ncc\\n\u00c2\u00aba\\nm Uj\\no\\nE\\nUj\\n0.\\nc\\no\\no\\n3\\nT3\\no\\n03\\nCD\\n\u00c2\u00a93\\n5\\n06\\nCD\\nCD\\n.c\\n2\\n\u00e2\u0096\u00a05\\n0\\nCD\\n2\\nC\\n0\\n\u00e2\u0080\u0098cd\\n.0\\nDC\\nE CD\\n3 CD\\nCO\\nCD\\n0\\nO\\n3\\na) ~o\\nCL\\nAppendix A National Emissions (1970 to 1998) A-37", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0237.jp2"}, "238": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nT3\\n0\\n3\\nC\\nO\\nCO\\nI\\n0\\nJ2\\nCO\\nS-^oo o 0000000000\\no 0000 O 00000\\nt\\nCO\\n\u00e2\u0080\u00a2o\\nCD\\n1 _\\nTD\\nC\\nk\\n\u00e2\u0096\u00a0o\\no\\no\\nLL\\nCD _\\nk_\\nO\\nO)\\n\u00e2\u0096\u00a0O c\\nI I\\nII\\n(0 Q.\\nQ.\\nCL \u00c2\u00b0S\\nd\\nCL\\nO\\n0.\\n08\\nO T-\\n\u00c2\u00a35^foo o oooo)Oooooo\u00e2\u0080\u0099~o\\n00\\nO O O O 0 O O C O COOOOOOP OOCOLO\\nCo CO CO IP CO\\nCM T-\\nO OOO^tOO-^- ^\u00e2\u0080\u00a2OOOOOOOCOCO^t\\nco co 00 J in n\\nC\\\\| T-\\nO OOO^OO^t ^\u00e2\u0080\u00a2OOOOOr-COOTCO O-\\nco 00 00 CO LO CO\\nC\\\\| 1-\\nOCM O C0O O o 5 o SS S^^ T\\nn Z Z Z Z Z ZZZZZ ZZ Z ZZ \u00c2\u00aeZZ\u00c2\u00ae (I 1 ^ZZZZ^O in\\nO CM O C0O O O CO CO CO OOOO\\nZZ Z ZZ\u00e2\u0080\u009d ZZZZZ ZZ Z ZZ ^ZZ\u00c2\u00ae 0l ^ZZZ7?)0) t\\nCM\\nOco o f-o c o cp CO 2^ cno)\\nzz z zz\u00e2\u0080\u009d zzzzz zz z zz ^zz^^Zzzzz^J\u00e2\u0080\u009d\u00e2\u0080\u009d\\nr- o\\n05 00 0 C0O 0 oO cn Dt( -inT-o\\nco zz z zz\u00e2\u0080\u009d ZZZZZ ZZ Z ZZ eo ZZ\u00e2\u0080\u009d\u00c2\u00b0\u00c2\u00b0^ZZZZ^\u00e2\u0080\u009d\u00e2\u0080\u009d\\nC0CM O 10 O O o Jo co \u00c2\u00bb3 jo r i;oo\\n2 2 22 22222 22 2 22\\nJO CNJ 0 100 0 OCNJ CNJ JNJ SNJ03CNJOO\\nZZ Z ZZ\u00e2\u0080\u009d ZZZZZ ZZ Z ZZ O zz co0o^ zzzz oj in co\\nS .9-\\n\u00e2\u0080\u009413\\nCL 12\\no\\ng -o 3\\n.2 \\\\p o xj\\nF CL\\no\\nCO\\nCO\\nC0\\n3\\nO\\nCD\\nC\\nm\\na3\\no\\nco\\nco\\no\\nCO\\nCO\\nCD\\no\\no\\nO\\n3\\nTJ\\nO\\nO\\n3\\nT3\\nO\\nCO\\nW\\nO\\n3\\nTO\\nO\\n\u00c2\u00b08 o Q-\\no\\n3\\nO\\no\\nc 0\\nCD 3\\nE\\n9-\\n3\\nc r\\nLU\\n.9\\n3 5\\nO CD\\no c\\nCD\\n01\\nCE CL\\nCD\\nC\\nO\\n9\\n3\\nu _\\nC CO\\nCO 2 s 5\\no t; .2 o\\n.c -3\\no O\\nCO\\nCD\\n_ O\\nCD CO\\nLU\\nw .E \u00c2\u00a30-0\\n2 s S 0 CD c\\nQ. O CD 53\\nCD [rt r~\\nlil 0 2 c 3\\nQ 0 Q W O\\n-4\\no\\n0\\nK\\nQC\\nO\\nI\\nI\\n\u00c2\u00ae8\\nUJ\\nO\\ne\\nco\\nc/3\\nc\\n_co\\nCL\\n03\\nC\\nE\\n|2\\n3\\nco\\nE\\n3\\na\\no\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094*\\nD\\nCL\\n08\\nE\\nCD\\nE\\n3\\na\\no\\nk_\\nQ)\\nQ.\\n08\\nE\\n3\\nCD\\nCD\\nCD\\nCD\\nO\\nCO\\ncO\\no\\nO CD O\\nE\\nCD\\n-C\\nt O\\no .2\\nE\\nc S\\ns\u00c2\u00bb\\nCD CD _\\nCL CO CL I- O JE\\nCD\\nCD\\nCD\\nk_\\no\\nCO\\nCD\\nO\\nE\\nCD\\n-C\\nO\\no\\nc\\nCD\\nCD\\nk_\\nO\\nc\\n3\\nS\\nD O\\nCD LU\\nCD CC\\n2 08\\nCO\\n_co\\nCD co\\nffl\\nCO\\nco\\nQ)\\nO\\no\\no\\no\\nQ\\nK\\nco\\n5\\nCD\\nif\\n2 co\\nCD c \u00c2\u00abS\\n0 h\\nO CL O\\n2 O CL\\nCD\\nD\\n\u00e2\u0096\u00a02\\n1\\nCD\\n\u00e2\u0096\u00a04\u00e2\u0080\u0094\\nco\\n1\\nQ)\\nCO\\n0)\\nGO\\nCO\\noa\\n03\\nQ)\\nCO\\nQ\\n3\\nH\\n_CL)\\nO\\n0\\n0\\nS S\\n0\\n3\\nO\\nc\\nQ 1\\nCD\\nO\\nCO\\nUJ\\n-j co\\nO co\\nJ O O\\nijj k\\nS 3 3\\nQ 9 9\\n_\\nQ CD D) CD\\nCC X\\no\\nco\\nCO CD\\nCD O\\n3\\nQ\\nr\\nCO\\nA-38 Appendix A National Emissions (1970 to 1998)", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0238.jp2"}, "239": {"fulltext": "National Air Pollutant Emission Trends, 1900-1998\\nT5\\nD\\n3\\nC\\n\u00e2\u0096\u00a03\\nC\\no\\n00\\nI\\n0)\\nn\\n03\\nT- CO CO\\nQ r- co co\\nn n t-\\nf CO T\u00e2\u0080\u0094 CM\\nCO 00 Tj- CM CM\\nCM CM CO K\\nrf CO\\n52 CO Co CO CO CO\\nCO CO Co CO CO K\\nt Co\\nrt Co\\nCM CM CO CO CO\\nCO CO\\nCo CO\\nM- Co\\nn. o\\nf M CO\\nr-^p5 0 )Kv-\\nCO CO N CM Co\\n0 03 \u00e2\u0096\u00a0M- CO\\nCo CO CO\\nI- CO\\nT- CO\\nT- CO\\nN T- CO T-\\nw Q o j t ono\\nCO CO CM CM 05 cm\\no o CO_ lo\\nco co\u00e2\u0080\u0099 CO\\nW Jl O) O) p O)\\nCM CM CO co N 03\\nco CO CO M-\\nco co\u00e2\u0080\u0098.co\\nOjCpCO^tM\u00e2\u0080\u0099^ COo\\nCM CM E T- xj- K\\nco 00 CO M\\nco co co\\nCMjlOlOo tPO\\nCM CM N N CM O\u00e2\u0080\u0099\\nN CO t\\nco co co\\n0 T- cm T- cm\\nO O h- N. Q\\nCO CO CM CM O CM\\nK N to\\nco CO* co\\nCO\\nUj\\nLU\\nC/)\\n0)\\nc\\na c\\n.p\\nts\\no 03\\nw w\\nco\\nO Q\\nD\\nCO\\no\\ncc\\nI\\nc\\no\\nT3\\n0\\nO\\noc\\nI\\nc\\no\\n(JO\\n0\\nCO\\nCO\\nfo\\na\\nw u=\\nw;\\n\u00e2\u0096\u00a0Q\\nSJ\\nCO\\nO\\n0\\n0\\n*c\\n0\\nc\\nO\\nJ\\n0\\nk\u00e2\u0080\u0094\\no\\nL.\\nk_\\nO)\\nk.\\n0\\n0\\nQC\\no\\nQC\\ne\\nCD\\ns\\no\\nlu\\nCO\\n2 5)\\nO co\\no\\no\\n3 .1\\n3\\no\\ny.\\nO)\\nCO\\nI I\\n03 03\\n03\\n3\\nco\\n*w_\\no\\n03\\n03\\nco\\no\\n0)\\no\\nk_\\no\\no\\nc/3\\no\\no\\n03\\no.\\nCO\\nCM\\nO\\n03\\no\\nN\\nn\\n03\\n_o\\nco\\n0)\\no\\n.Q\\nCO\\n0)\\nQ.\\n1\\n\u00e2\u0096\u00a0o\\nCD\\n0\\nO\\nO\\n03\\nv_\\n3\\nO\\no\\n03\\n0\\nJD\\nO\\nC\\nT3\\n3\\nO\\nO\\n03\\nJZ\\nCO\\nc\\no\\n0\\nCO\\nE\\n0\\nc\\n0\\nc\\no\\no\\n0\\nE\\n0\\nc\\no\\no\\nCD\\nE\\nTO\\n!_\u00e2\u0080\u00a2 C\\nco co\\n03 w\\n3\\no\\n\u00e2\u0080\u00a2e\\no\\nSI\\n03\\nco\\nE\\nCO\\nCO\\n03\\nO\\no\\nLO 03\\no\\nco\\nSI C/3\\nc\\nC/3 O\\na\\n-2? c/3\\nw\\n_2\\nII\\nco 03\\nCO\\nO =i_\\no CD\\nII\\nP\\nc E\\n03 03\\nC/3\\n2 o3\\nQ.\\n03 C\\nO\\nw O\\no 2\\n03\\nTO\\n2 o\\n03 c-\\nN\\n03\\nO\\nAppendix A National Emissions (1970 to 1998) A-39", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0239.jp2"}, "240": {"fulltext": "[This page intentionally left blank.]", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0240.jp2"}, "241": {"fulltext": "Index\\nAcid Deposition Control.3-5\\nacid rain 1-2, 4-1\\nAcid Rain Program. 1-3, 3-2, 3-8, 4-2\\nAerometric Information Retrieval System 5-5, 5-11\\naerosol .1-2\\nAFS 5-5, 5-6\\nair toxic emissions ES-1, 1-1, 7-1,7-2, 7-3, 7-5\\nAIRS. 5-5,5-11\\nAIRS Facility Subsystem .5-5\\nallother.1-3, 2-2, 2-3\\nammonia ES-1, ES-3, 1-1, 2-1,2-3, 2-16, 2-23, 3-1,3-16, 3-29, 5-2, 9-1,\\nA-37\\nammonium nitrate 1-2, 2-3, 2-4, 3-14, A-37\\nammonium sulfate 1-2,2-3,2-4,3-14\\nanthropogenic. ES-3, 2-8, 3-3, 6-1, 7-3, 8-1\\nAP-42.4-4,5-11,7-3,7-6\\narea source 2-2, 2-3, 2-6, 3-11,4-6, 5-1, 5-5, 5-7, 5-8, 5-10, 5-11, 5-12,\\n5-15, 7-1, 7-2, 7-3, 7-4, 7-5, 7-6, 7-15, 7-23, 7-24, 7-45, 7-46,\\n7-47,7-48,7-51\\nBEA.4-2,4-3,5-5,5-7,5-8,5-11,5-12,8-3,8-4\\nBEIS2.6-1\\nbiogenic ES-1, 1-6, 2-3, 3-3, 3-16, 6-4, A-39\\nbiogenic emissions. ES-3, 1-1, 1-4, 6-1, 6-2, 6-3, 6-5, 6-6\\nBiogenic Emissions Inventory System .6-1\\nbituminous coal 2-1, 2-2, 3-10, 3-12, 3-13, 3-14, 3-15, A-7, A-19, A-23,\\nA-29, A-34\\nBudget Trading Program .3-2\\nBureau ofEconomic Analysis .4-2, 5-5, 5-10, 5-11, 8-3, 8-4\\nCAA.ES-1, ES-2, 1-1, 3-1, 3-2, 3-5, 4-2, 7-1, 7-2, 7-3, 7-4, 7-5, 7-6\\nCAAA.ES-2, 1-3, 3-2, 3-5, 3-6. 3-7, 4-1, 4-3, 5-5\\nCalifornia Air Resources Board .5-9\\ncarbon dioxide .ES-1, 8-1, 8-5, 8-8, 8-9, 8-10, 9-1\\ncarbon monoxide ES-1, ES-3, ES-4, ES-6, 1-1, 1-5, 2-1,2-9, 2-17, 3-1,\\n3-2, 3-9, 3-17,5-2, 9-1, A-2\\ncarcinogen .7-1\\ncarcinogenesis .1-2\\ncardiovascular disease .1-1, 1-2, 7-1\\nCEM.1-3,5-11,5-14\\nCensus Bureau 7-4, 7-6\\nCensus of Agriculture.2-5, 5-8, 5-11\\nCFCs.3-3, 8-1, 8-2\\nCH 4 .ES-1, 3-3, 8-1, 8-2, 8-5, 9-1, 9-3, 9-11, 9-12, 9-13, 9-14, 9-15\\nchemical and allied product manufacturing 1-6, 2-2, 2-3, 2-6, 2-7, 3-1,\\n3-3, 3-5, 3-6, 3-9, 3-10, 3-11, 3-12, 3-13, 3-14, 3-15, 3-16, 4-3,\\n4-5,4-7,5-11\\nchlorofluorocarbons 3-3, 8-1\\nClean Air Act.ES-1, 1-1, 3-1,4-1, 7-1\\nClean Air Act Amendments of 1990 .ES-2, 1-3, 3-2, 4-1\\nCNG. 5 2 5 4\\nCO ES-1, ES-2, ES-6, 1-1, 1-3, 1-4, 2-1, 2-2, 2-4, 2-6, 2-8, 3-1,3-2, 3-4,\\n3-5, 3-6, 3-7, 3-8, 3-9, 3-17, 3-18, 3-19, 5-2, 5-3, 5-4, 5-5, 5-11,\\n5-12, 9-1, 9-4, 9-5, 9-6, 9-7, 9-8, 9-9, 9-10, 9-15, A-2\\nC0 2 ES-1, 8-1, 8-2, 8-3, 8-5, 8-6, 9-1, 9-3, 9-11,9-12, 9-13, 9-14, 9-15\\nCode of Federal Regulations.\\ncompressed natural gas.\\ncontinuous emission monitoring.\\n5-2\\n1-3\\nCORINAIR. 9-1,9-4\\ncriteria pollutant ES-1, ES-3, 1-1, 1-3, 1-4, 2-4, 3-1, 5-1,5-2, 5-3, 5-5,\\n5-6, 5-7, 7-6, 9-1\\nDepartment of Agriculture .ES-2, 5-8\\nDepartment of Energy. 3-8, 4-3, 5-8, 5-10, 8-4\\ndesulfurization .3-5, 3-7,4-1, 4-3, 4-4,4-11\\nDOE. 4-3,5-8,5-10,5-11,8-2,8-3,8-4\\nEconomic Growth Analysis System .2-5, 5-3, 5-10\\nEEA .9-1,9-11,9-12,9-13,9-14,9-15\\nEF1G. 1-2, 1-4\\nEGAS.2-5, 5-3, 5-4, 5-7, 5-8, 5-9, 5-10, 5-11\\nEIIP.5-9\\nelectric utility.ES-1, 1-3, 2-1,2-2, 2-3, 3-4, 7-1, 7-2, 8-1, 8-2\\nEMEP.. 9-1, 9-4\\nEmission Factor and Inventory Group 1-2, 2-4\\nEmission Inventory Improvement Program .5-9\\nEmission Tracking System.1-3\\nEmission Trends Report.1-2, 1-3, 2-5\\nenvironmental impacts.7-1\\nEnvironmental Protection Agency ES-1, 1-1,2-2, 3-1,4-1, 5-1, 6-1, 7-1,\\n8-1\\nEPA ES-2, 1-1, 1-2, 1-3, 1-4, 2-2, 2-3, 2-4, 3-1, 3-3, 3-5, 3-6, 3-7, 3-8,\\n4-1, 4-2. 4-3, 4-4, 5-1, 5-4, 5-5, 5-6, 5-8, 5-9, 5-10, 6-1, 7-1,7-2,\\n7-3, 7-4. 7-5. 7-6, 8-1, 8-2, 8-3\\nETC/AEM .9-1\\nethane. 1-4, 3-3\\nETS. 1-3,5-14\\nEuropean Environment Agency .5-10, 9-1, 9-2\\neutrophication.1-1\\nFAA 5-3, 5-4\\nFactor Information Retrieval. 7-3,7-6\\nFederal Aviation Administration.5-3, 5-10, 8-4\\nFederal Government.3-1, 3-17, 3-18\\nFederal Information Processing Standards .5-7\\nFederal Power Act .4-2\\nFIPS .5-7\\nFIRE. 7-3, 7-6\\nfossil fuel ES-2, 1-3, 3-4, 3-5, 4-1,4-2, 8-1, 8-2, 8-3, 8-5, 8-6, 9-1, 9-4,\\n9-5, 9-6, 9-7, 9-8, 9-9, 9-10\\nFramework Convention on Climate Change.8-1\\nfuel combustion 1-6,2-3,3-1,3-4,3-5,4-3,5-8,7-5,8-2,9-15\\nelectric utility.1-6, 2-2, 2-3, 2-6, 2-7, 3-4, 3-9, 3-10, 3-11,3-12,\\n3-13,3-14, 3-15,3-16, 8-6, A-22\\nindustrial 1-6,2-2,2-3,2-6,2-7,3-3,3-4,3-9,3-10,3-11,3-12,\\n3-13,3-14,3-15,3-16, 4-5, 4-7\\nother.. 1-6, 2-2, 2-6, 2-7, 3-4, 3-9, 3-10, 3-11, 3-12, 3-13, 3-14, 3-15,\\n3-16\\nfugitive dust ES-1, ES-2, ES-3, ES-4, 1-4, 1-6, 2-4, 2-5, 3-3, 3-8, 3-12,\\n3-13,3-14,3-26, 3-27,7-29\\nGACT.7-1,7-2, 7-5, 7-6\\nGCVTC .4-2,5-1,5-5,5-9,5-11,5-13\\nGDP.ES-1, 3-2\\ngenerally achievable control technology.7-1\\ngeogenic ES-4, 1-4, 1-6, 3-3, 3-13, 3-14, 7-28, 7-31, 7-34, 7-37, 7-40,\\nA-18, A-27, A-33\\ngeothermal energy.9-1, 9-4, 9-5, 9-6, 9-7, 9-8, 9-9. 9-10\\nIndex 1", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0241.jp2"}, "242": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nGrand Canyon Visibility Transport Commission .4-2, 4-6, 5-1, 5-11\\nGreat Depression .ES-1,3-4\\ngreenhouse gas emissions ES-1, 1-1, 8-1, 8-2, 8-3, 8-4, 8-5, 8-7, 8-8, 9-1,\\n9-4, 9-11,9-12,9-13,9-14, 9-15\\ngross domestic product. ES-1, 3-2, 3-21\\ngross state product .5-7\\ngrowth factor 5-3, 5-4, 5-5, 5-7, 5-8, 5-9, 5-11\\nGSP .5-7\\nHAPs ES-1, 7-1, 7-2, 7-3, 7-4, 7-5, 7-6, 7-7, 7-9, 7-10, 7-14, 7-15, 7-18,\\n7-22, 7-23, 7-24, 7-25, 7-27, 7-30, 7-33, 7-36, 7-39, 7-45, 7-46,\\n7-47,7-48,7-49,7-50, 7-51\\nhazardous air pollutants .ES-1, ES-3, 7-1, 7-2, 7-7\\nHCFCs .8-1, 8-2, 8-5\\nHDDV .2-1,3-14,5-9, 5-10, A-32\\nHealth, Education, and Welfare .3-1\\nheavy-duty truck.3-6\\nheavy-duty vehicle .5-9\\nMFCs .ES-1, 8-1, 8-2, 8-5\\nhistoric emissions. ES-2, 1-4, 1-5, 3-1, 3-2\\nhydrocarbon .3-2,3-3,3-17,3-18\\nhydrochlorofluorocarbons.8-1\\nhydrofluorocarbons.ES-1, 8-1\\nindustrial.1-3, 2-1, 2-2, 2-3, 3-4, 3-5\\nindustrial processes. ES-1, 2-3, 3-1, 3-5, 3-6, 8-2\\nindustrial S0 2 .4-5, 4-6, 4-7\\nIntegrated Urban Air Toxics Strategy. 7-2, 7-4, 7-5, 7-6, 7-10\\nIntergovernmental Panel on Climate Change .8-1\\ninternational emissions. 1-1, 9-1\\nIPCC.8-1, 8-3, 8-4\\nlanding-takeoff operations .5-3\\nLDGVs. 2-1, 2-2, A-32\\nLDT .3-6,3-17,3-18\\nLDV. 3-6,3-17\\nlead ES-1, ES-3, ES-4, ES-6, 1-1, 1-2, 2-1, 2-3, 2-15, 3-1, 3-12, 3-15, 5-4,\\n7-2, 7-8, 7-10\\nlight-duty gasoline vehicle .1-6, 2-1,2-2\\nlight-duty truck.3-6, 3-17, 3-18\\nlight-duty vehicle. 3-6,3-17\\nliquefied petroleum gas.5-2, A-5, A-10, A-17, A-27, A-33\\nLPG .5-2, 5-4, 8-6\\nMACT .2-2, 2-5, 5-8, 7-1, 7-2, 7-3, 7-4, 7-5, 7-6\\nmajor source 1-1, 3-2, 4-2, 4-8, 4-10, 7-1, 7-2, 7-4, 7-5, 7-11, 7-45, 7-47,\\n7-48,7-51,9-1,9-15\\nManufacturing Consumption of Energy.8-2\\nmaximum achievable control technology.2-2, 5-8, 7-1\\nmetals processing 1-6, 2-2, 2-3, 2-6, 2-7, 3-1, 3-5, 3-9, 3-10, 3-11, 3-12,\\n3-13,3-14, 3-15,3-16,4-5,4-7\\nmethane ES-1, 1-4, 3-3, 8-1, 9-1\\nmethodology. ES-4, 1-2, 1-3, 3-5,4-1, 5-7, 8-1, 8-3\\nmetropolitan statistical area .7-4\\nmiscellaneous ES-4, 1-3, 1-4, 1-6, 2-1,2-2, 2-3, 2-6, 2-7, 3-1, 3-3, 3-8,\\n3-9, 3-10, 3-11, 3-12, 3-13, 3-14, 3-16\\nMOBILE model .5-1,5-9,5-10,5-11\\nmobile sources ES-1, 1-1, 5-1, 7-1, 7-2, 7-3, 7-4, 7-5, 7-15, 7-23, 7-24,\\n7-45,7-46,7-47,7-48,7-51\\nmolecular weight .1-4\\nN20 .ES-1, 8-1, 8-2, 9-1\\nNAA.ES-2, 1-3, 5-5, 5-7\\nNAAQS ES-2, 1-1, 3-1, 3-2, 3-3, 3-5\\nNAPAP. 1-3, 2-4, 4-2, 4-6, 5-3, 5-4, 5-11, 5-12, 5-13\\nNational Acid Precipitation Assessment Program 1-3, 2-4, 4-2, 5-3\\nNational Air Pollution Control Administration.3-1\\nNational Ambient Air Quality Standards ES-2, 1-1, 3-1\\nNational Emission Trends. 1-2, 3-1, 4-2, 5-1\\nnational emissions ES-4, ES-5, ES-6, 1-2, 3-1, 3-3, 3-4, 3-5, 3-7, 3-8,\\n7-44, 7-45,7-46, 7-51\\nNational Particulate Study .3-3\\nNational Toxics Inventory.7-3\\nnatural gas 3-10, 3-12, 5-2, 5-8, 8-1, 8-2, 8-3, 8-5, 8-6, A-5, A-8, A-10,\\nA-17, A-20, A-27, A-33\\nnatural sources ES-4, 1-4, 1-6, 2-3, 2-6, 2-7, 3-3, 3-11, 3-13, 3-14, 3-16\\nNET 1-2, 2-3, 3-14, 4-2, 4-6, 5-1, 5-3, 5-4, 5-5, 5-6, 5-7, 5-8, 5-9, 5-11,\\n5-12\\nneurological impairments. 1-2, 7-1\\nnew source performance standards.ES-2, 3-2\\nNH 3 ES-1, 1-1, 1-2, 1-4, 2-1, 2-3, 2-4, 2-7, 2-8, 3-1, 3-2, 3-3, 3-4, 3-6,\\n3-7, 3-8, 3-14, 3-19, 5-2, 5-4, 5-5, 5-7, 5-8, 9-1, 9-3, 9-4, 9-5,\\n9-6, 9-7, 9-8, 9-9, 9-10, A-37\\nnitrate. 1-1, 1-2\\nnitric oxide. ES-3, 1-1, 1-4, 6-1, 6-3, 6-4\\nnitrogen dioxide. 1-1, 1-4\\nnitrogen oxides ES-1, ES-3, ES-4, ES-5, 1-1, 1-4, 2-1, 2-2, 2-10, 2-18,\\n3-1, 3-10, 3-17, 3-18, 3-21, 3-23, 4-1, 5-1, 6-5, 9-1, A-7\\nnitrous oxide.ES-1, 8-1, 8-8, 9-1\\nNMVOCs.9-1,9-3,9-4,9-5,9-6,9-7,9-8,9-9,9-10\\nNO .1-1, 1-4, 6-1\\nN0 2 1-1, 1-4\\nnon-road engines and vehicles ES-2, 1-3, 1-6, 2-1,2-2, 2-3, 2-6, 2-7, 3-1,\\n3-6, 3-7, 3-8, 3-9, 3-10, 3-11, 3-12, 3-13, 3-14, 3-15, 3-16, 5-2,\\n5-3, 5-4, 5-7, 5-11, 5-12, 5-13, 7-3, 7-15, 7-23, 7-24, A-5, A-9,\\nA-17, A-22, A-26, A-32, A-36, A-39\\nnonattainment area. ES-2, 1-3, 5-5\\nnonfugitive dust ES-3, ES-5, 1-4, 2-3, 2-13, 2-14, 3-3, 3-4, 3-6, 3-7, 3-8\\nnonmethane 3-3,3-18\\nnonmethane volatile organic compounds .9-1\\nnonreactive organic compounds.1-1\\nNONROAD model.5-2,5-3,5-4,5-11\\nNOx ES-1, ES-5, 1-1, 1-2, 1-3, 1-4, 2-1, 2-2, 2-3, 2-4, 2-6, 2-8, 3-1,3-2,\\n3-3, 3-4, 3-5, 3-6, 3-7, 3-8, 3-14, 3-17, 3-18, 3-19, 4-1, 5-1,5-2,\\n5-3, 5-4, 5-5, 5-7, 5-8, 5-9, 5-10, 5-11, 5-12, 5-14, 9-1, 9-3, 9-4,\\n9-5, 9-6, 9-7, 9-8, 9-9, 9-10, 9-15\\nNPI.3-3\\nNSPS .ES-2, 3-2, 3-5, 3-6\\nNTI 7-3,7-4.7-5,7-6,7-7,7-11,7-15,7-23,7-24,7-25,7-27,7-42,7-44,\\n7-45, 7-46, 7-47, 7-48, 7-49, 7-50, 7-51\\n0 3 1-1, 1-2, 3-2, 3-3, 8-1\\nOffice of Mobile Sources .3-18, 5-2, 5-10\\nOffice of Transportation and Air Quality 5-2,7-3\\nOMS. 5-2, 5-10\\non-road vehicles ES-2, 1-3, 1-6, 2-1, 2-2, 2-3, 2-4, 2-6, 2-7, 3-1, 3-3, 3-6,\\n3-7, 3-9, 3-10, 3-11, 3-12, 3-13, 3-14, 3-15, 3-16, 4-3, 4-4, 4-11,\\n5-4, 5-7, 5-8, 5-9, 5-11, 7-3, 7-5, A-4, A-9, A-16, A-21, A-26,\\nA-32, A-35, A-38\\norganic compounds. 1-4, 3-3\\nOTAG.4-2, 4-6, 5-1, 5-3, 5-5, 5-9, 5-11, 5-12, 5-13\\nOTAQ.5-2, 5-3, 5-4, 5-10, 5-11, 7-3\\nother industrial processes 1-6, 2-2, 2-3, 2-6, 2-7, 3-1, 3-5, 3-6, 3-9, 3-10,\\n3-11, 3-12, 3-13, 3-14, 3-15, 3-16, 4-5, 4-7, 7-25, A-3, A-8,\\nA-13, A-20, A-24, A-30, A-35, A-38\\noxygen .1-1\\noxygenated fuel. ES-1, 2-1, 5-2\\nozone 1-1, 1-2, 3-2, 5-5, 8-1\\nOzone Transport Assessment Group.4-2, 5-1, 5-11\\nPART5 .4-4\\nparticulate matter ES-1, ES-3, ES-4, ES-5, 1-1, 1-2, 2-1, 2-3, 2-13, 2-14,\\n3-1, 5-2\\nparts per million.3-2\\nPb ES-1, ES-2, ES-6, 1-1, 1-2, 1-3, 1-4, 2-1, 2-3, 3-1, 3-2, 3-3, 3-4, 3-6,\\n3-7, 3-8, 5-4, 5-6, 5-11,7-2\\nPEI.1-2, 1-3, 2-4, 4-6, 5-1, 5-5, 5-6, 5-7, 5-9, 5-11, 5-12, 5-13, 5-15\\nperfluorocarbon .ES-1, 8-1\\nperiodic emission inventory .1-2, 2-4, 5-1\\npetroleum and related industries 1-6, 2-2, 2-3, 2-6, 2-7, 3-1, 3-3, 3-5, 3-6,\\n3-9, 3-10, 3-11,3-12, 3-13, 3-14, 3-16, 4-5, 4-7, 7-25, 7-27,\\n7-30, 7-33, 7-36, 7-39, A-3, A-8, A-12, A-20, A-24, A-30, A-37\\nPFCs.ES-1, 8-1\\nphotochemical oxidants 1-1, 1-5, 3-2, 3-3\\n2 Index", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0242.jp2"}, "243": {"fulltext": "National Air Pollutant Emission Trends, 1900 1998\\nplain language 1-3\\nPM .ES-1, ES-2, 1-1, 1-2, 3-5, 3-6, 5-2, 5-3, 5-8, 9-1\\nPM 10 ES-1, ES-3, ES-4, ES-5, 1-1, 1-3, 1-4, 2-1,2-3, 2-4, 2-7, 2-8, 2-13,\\n3-1,3-2, 3-3, 3-4, 3-5, 3-6, 3-7, 3-8, 3-13, 3-18, 3-19, 3-26, 5-2,\\n5-3, 5-4, 5-5, 5-11,9-1,9-15, A-23\\nPM 1S ES-1, ES-3, 1-1, 1-2, 1-4, 2-1,2-3, 2-4, 2-7, 2-8, 2-14, 2-21,2-22,\\n3-1,3-2, 3-3, 3-4, 3-6, 3-7, 3-8, 3-14, 3-19, 3-27, 5-2, 5-3, 5-5,\\n5-11, 9-1, 9-15, A-29\\npoint source 1-4, 2-1,2-2, 2-3, 2-4, 2-6, 3-2, 4-6, 5-1,5-5, 5-6, 5-7, 5-8,\\n5-11,5-12, 5-15. 7-1,7-15, 7-23, 7-24, 7-46\\nppm 3-2,3-7,3-17,3-18\\nprecursor. ES-1, 1-1, 1-2, 5-6, 9-1\\nPresident Clinton 1-3\\nRACT.3-2\\nreasonably available control technology.3-2\\nreformulated gasoline. ES-1, 2-1,5-2\\nRegional Economic Models, Inc. 5-7, 5-10\\nRegulatory Support Document.5-4\\nReid vapor pressure ES-1,2-1,5-2\\nREM1 5-7, 5-8\\nresidential wood combustion ES-2, 1-6, 2-4, 3-3, 3-4, 3-9, 3-11,3-13,\\n3-14,7-27\\nrespiratory illness .1-1, 1-2, 7-1\\nRFG .5-2\\nRSD 5-4,5-10\\nrural 2-4,7-4,7-5,7-11,7-15,7-43,7-44,7-45,7-46\\nRVP ES-1,5-2, 5-3\\nSCC 1-4,1-6,5-2,5-3,5-4,5-5,5-7,5-8,5-11,5-12\\nsection 406 4-1, 4-3\\nSEDS .1-3\\nSF 6 .ES-1, 8-1,8-2, 8-5\\nshort tons ES-3, ES-5, ES-6, 1-4,2-6,2-8,3-9,3-10,3-11,3-12,3-13,\\n3-14, 3-15, 3-16, 4-3, 4-7, 6-2, 6-3\\nSIC.4-3, 5-7, 5-8, 7-4\\nSIP .1-2, 3-2, 5-1\\nSO, ES-1, ES-2, ES-5, 1-1, 1-2, 1-3, 1-4, 2-1,2-2, 2-3, 2-4, 2-6, 2-8, 3-1,\\n3-2, 3-3, 3-4, 3-5, 3-6, 3-7, 3-8, 3-14, 3-19, 4-2, 4-4, 4-7, 5-1,\\n5-2, 5-4, 5-5, 5-11,5-14, 9-1,9-3, 9-4, 9-5, 9-6, 9-7, 9-8, 9-9,\\n9-10, 9-15\\nsolvent utilization 1-6, 2-2, 2-3, 2-6, 2-7, 3-1, 3-5, 3-9, 3-10, 3-11,3-12,\\n3-13, 3-14, 3-16, 4-3, 4-5, 4-7, A-3, A-8, A-13, A-21, A-25,\\nA-31, A-38\\nsource category ES-1, 1-1, 1-4, 1-6, 2-1, 2-2, 2-3, 2-6, 3-2, 3-8, 4-7, 5-2,\\n5-8,7-3,7-5,7-6,9-14.9-15\\nSource Classification Code. 1-4, 5-2\\nspatial emissions.2-4, 6-1, 7-4\\nsport utility vehicle.3-6\\nStandard Industrial Classification. 4-3, 7-4\\nStandard Industrial Classification code .5-7\\nState Energy Data System. 1-3\\nState Implementation Plan .1-2, 3-2, 5-1\\nstationary sources.1-1, 3-2, 3-4, 7-1,7-2, 7-4, 7-5, 8-5\\nstorage and transport.1-6, 2-2, 2-3, 2-6, 2-7, 3-1, 3-5, 3-9, 3-10, 3-11,\\n3-12, 3-13, 3-14, 3-16, 4-3, 4-5, 4-7\\nsulfate. 1-2, 3-7\\nsulfate aerosols.1-2\\nsulfur .3-7\\nsulfur dioxide ES-1, ES-3, ES-4, ES-5, 1-1,2-1,2-2,2-12,2-20,3-1,3-7,\\n4-1,5-1,9-1\\nsulfur hexafluoride.ES-1, 8-1\\nSUV .3-6\\nTier 1 1-3, 1-4, 1-6, 2-2, 2-3, 3-5, 3-13, 3-14, 3-15, 3-16,4-5, 7-5, 7-6,\\n7-25, 7-26, 7-27\\nTier 2 1 -4, 1 -6, 4-5, 5-5, 7-5, 7-6, 7-27\\nTier 3 .1-4, 3-12, 4-5, A-l, A-22\\nTier 4 .1-4\\nTier I standards. 2-1, 3-7\\nTier II standards .1-4, 3-6, 3-7\\nTier level. 1-4\\nTitle IV.3-2, 3-5, 4-1,4-2\\ntotal particulate.9-1\\ntotal suspended particulate.3-2\\ntoxic air pollutants .7-1\\nToxics Release Inventory .7-3\\nTRI.7-3\\nTSP. 3-2, 3-5\\nUNFCCC .8-1\\nunleaded gasoline.3-7\\nurban 7-1,7-2,7-4,7-5,7-10,7-11,7-15,7-24,7-27,7-43,7-44,7-45,\\n7-46\\nUSDA. ES-2, 5-8, 5-11\\nutilities .2-1\\nvehicle miles traveled.ES-1, 2-1, 3-2, 5-11\\nVMT.ES-1,2-1, 3-2, 3-6, 3-7, 5-11\\nVOC ES-1, ES-2, ES-5, 1-1, 1-3, 1-4, 2-1, 2-2, 2-4, 2-6, 2-8, 3-1, 3-2,\\n3-3, 3-4, 3-5, 3-6, 3-7, 3-17, 3-18, 5-2, 5-3, 5-4, 5-5, 5-8, 5-11,\\n6-1, 9-1\\nvolatile organic compounds ES-1, ES-3, ES-4, ES-5, 1-1,2-1, 2-11,2-19,\\n3-1,3-17, 3-18, 5-2, 6-1,6-2, 6-4, 6-6, 9-1\\nwaste disposal and recycling 1-6, 2-2, 2-6, 2-7, 3-1,3-5, 3-9, 3-10, 3-11,\\n3-12, 3-13, 3-14, 3-15, 3-16, 4-5, 4-7\\nwind erosion.ES-4, 1-4, 1-6, 2-3, 3-8, 3-13, 3-14, A-27, A-33\\nIndex 3", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0243.jp2"}, "244": {"fulltext": "TECHNICAL REPORT DATA\\n(PLEASE READ INSTRUCTIONS ON THE REVERSE BEFORE COMPLETING)\\n1. REPORT NO. 2.\\nEPA-454/R-00-002\\n3. RECIPIENT\u00e2\u0080\u0099S ACCESSION NO.\\n4. TITLE AND SUBTITLE\\nNATIONAL AIR POLLUTANT EMISSION TRENDS REPORT,\\n1900-1998\\n5. REPORT DATE\\n3/1/2000\\n6. PERFORMING ORGANIZATION CODE\\nUSEPA/OAQPS/EMAD/EFIG\\n7. AUTHOR(S)\\nSHARON V. NIZICH, ANNE A. POPE, LAUREL M. DRIVER (USEPA)\\n8. PERFORMING ORGANIZATION REPORT NO.\\n9. PERFORMING ORGANIZATION NAME AND ADDRESS\\nU.S. ENVIRONMENTAL PROTECTION AGENCY\\nOFFICE OF AIR QUALITY PLANNING AND STANDARDS\\nEMISSION FACTOR AND INVENTORY GROUP (MD-14)\\nRESEARCH TRIANGLE PARK, NC 27711\\n10. PROGRAM ELEMENT NO.\\n11. CONTRACT/GRANT NO.\\n68-D7-0067\\n12. SPONSORING AGENCY NAME AND ADDRESS\\nDIRECTOR, OFFICE OF AIR QUALITY PLANNING AND STANDARDS\\nOFFICE OF AIR AND RADIATION\\nUS ENVIRONMENTAL PROTECTION AGENCY\\nRESEARCH TRIANGLE PARK, NC 27711\\n13. TYPE OF REPORT AND PERIOD COVERED\\nTECHNICAL 1900-1998\\n14. SPONSORING AGENCY CODE\\nEPA/200/04\\n15. SUPPLEMENTARY NOTES\\n16. ABSTRACT\\nThe Emission Factor and Inventory Group (EFIG) annually produces a publication on the trends in emissions of criteria\\npollutants. The emission estimates developed and included in the Emission Trends database have been utilized to\\nsupport development of the National Particulates Inventory, in support of recent evaluations of the particulate matter\\nand ozone NAAQS, in support of the National Air Toxics Assessment, and to satisfy requirements under CAAA406(g).\\nIncluded in this report are criteria, toxics, biogenics, greenhouse gases, and international criteria emission estimates.\\nKEYWORDS/DESCRIPTORS: CRITERIA AIR POLLUTANT, EMISSIONS TRENDS, GREENHOUSE GASES,\\nBIOGENICS, AIR TOXICS, INTERNATIONAL EMISSIONS.\\n17. KEY WORDS AND DOCUMENT ANALYSIS\\na. DESCRIPTORS\\nAIR EMISSION TRENDS OZONE\\nAIR POLLUTION PARTICULATE MATTER\\nAMMONIA SULFUR DIOXIDE\\nBIOGENICS TOTAL SUSPENDED PARTICULATE\\nCANADA TOXIC COMPOUNDS\\nCARBON MONOXIDE VOLATILE ORGANIC COMPOUNDS\\nNITROGEN DIOXIDE\\nNITROGEN OXIDES\\nb. IDENTIFIERS/OPEN ENDED TERMS\\nAIR POLLUTION CONTROL\\nAIR POLLUTION RESEARCH\\nAIR POLLUTION TRENDS\\nc. COSATI FIELD/GROUP\\n18. DISTRIBUTION STATEMENT\\nUNLIMITED\\nUNCLASSIFIED\\n21. NO. OF PAGES\\n236\\nUNCLASSIFIED\\n22. PRICE", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0244.jp2"}, "245": {"fulltext": "", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0245.jp2"}, "246": {"fulltext": "LIBRARY OF CONGRESS", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0246.jp2"}, "247": {"fulltext": "", "height": "4272", "width": "3070", "jp2-path": "nationalairpollu00unit_0247.jp2"}, "248": {"fulltext": "X 2 C; \u00e2\u0080\u0099Vf-saX A\\ntf. c \u00e2\u0080\u0098^\u00c2\u00ab;e C \u00c2\u00b0.v -i* \u00c2\u00b0v 0021^,,- V,\\nWJ\\no* 4^\\ni V* \u00e2\u0080\u00a2*4Sit -iJil sJBl* 3\\nA*\\nX#\\nv l\\n\\\\l// %0 y.\\no\\n\u00e2\u0096\u00a04,0\\nv r\u00c2\u00bb\\n\u00c2\u00b0o, %r A\u00c2\u00ab\\n\u00e2\u0080\u0098tv -pv*\\nA; 4k- A Tx A^ 4 J Jff\\nx- wf/ X ***vNrs\\n\u00c2\u00abV V^ X A^aK\\ni- AU. ^5L v 1\\nU. j. ^Xvyjr** V* r\u00c2\u00bb XA/Jj v o V o 4- 0 j*\\n,V- 0 X\u00e2\u0080\u0098* 1 \u00c2\u00b0s^\\n$St\u00c2\u00a9 A A\\\\\u00c2\u00ae/n, \u00e2\u0096\u00a0f-\\nil \\\\A :mmi X M; X#\\n\u00c2\u00abas* v4 \\\\Ww* X SI: V V oj\\nOl* V \u00e2\u0080\u00a20-V\u00e2\u0080\u0099 OU -O\\nf^\u00c2\u00b0C", "height": "4300", "width": "3117", "jp2-path": "nationalairpollu00unit_0248.jp2"}, "249": {"fulltext": "o p .S? i***^ ^\u00c2\u00abo p .V c**\\n^.VTT* v\\n__,,_. tjr cr\\nK; \\\\t-o* 0 \u00c2\u00abs\u00c2\u00a3fr\u00c2\u00ab(a w ssssfe* 1 ^o\\nv 5 -v *.\u00e2\u0080\u0099aly v ^\u00e2\u0080\u0098flllK? *3S\u00c2\u00a7u\u00c2\u00bb\u00c2\u00bb\\n?\u00c2\u00a3gk\\\\ :lMk\\\\\\\\f ff*** aV4\\nv:^;5v\u00c2\u00b0 11\\nW \u00c2\u00abfe^\\nlP L.\\ns. 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