Reducing Indoor Exposure to Particle Pollution from Outdoor Sources Policies and Programs for Improving Air Quality in Homes

Total Page:16

File Type:pdf, Size:1020Kb

Reducing Indoor Exposure to Particle Pollution from Outdoor Sources Policies and Programs for Improving Air Quality in Homes Reducing Indoor Exposure to Particle Pollution from Outdoor Sources Policies and Programs for Improving Air Quality in Homes JANUARY 2020 The Environmental Law Institute gratefully acknowledges the assistance of many individuals who provided information for this report and reviewed earlier drafts. Funding for the report was provided by the U.S. Environmental Protection Agency. The contents of the report are the responsibility of ELI. The views expressed herein should not be attributed to EPA, nor should any official endorsement be inferred. The Environmental Law Institute (ELI) makes law work for people, places, and the planet. Since 1969, ELI has played a pivotal role in shaping the fields of environmental law, policy, and management, domestically and abroad. Today, in our fifth decade, we are an internationally recognized, nonpartisan research and education center working to strengthen environmental protection by improving law and governance worldwide. Reducing Indoor Exposure to Particle Pollution from Outdoor Sources: Policies and Programs for Improving Air Quality in Homes © 2020 Environmental Law Institute®, Washington, D.C. All rights reserved. Cover Photos: Manfredxy, Chuangz, ssuaphotos, Thomas Oswald/Shutterstock.com Contents Executive Summary .................................................................................................................................. i Chapter One: Introduction ....................................................................................................................... 1 Health Effects of Particulate Matter ............................................................................................. 2 Ambient Particulate Matter in the United States .......................................................................... 5 Reducing Indoor Exposure to Particulate Matter from Outdoor Sources ...................................... 7 Scope and Organization of the Report .......................................................................................... 8 Chapter Two: Reducing Exposure to Outdoor Particulate Matter in New Homes .................................... 10 Part I: Strengthening Standards for New Residential Construction ..................................................... 10 High-Efficiency Filtration and Related Building Practices to Reduce Indoor Exposures ................ 11 Building Codes: Strengthening Minimum Residential Construction Requirements ...................... 15 Green Building Codes: Going Beyond Minimum to Reduce Indoor PM Exposures ....................... 25 Requirements for Publicly-Funded Residential Construction ...................................................... 29 Discussion .................................................................................................................................. 31 Part II: Addressing Local PM Sources and New Residential Construction: High-Volume Roads ........... 34 Near-Road Exposures: Nature and Extent of the Problem .......................................................... 35 Practices for Reducing Near-Road Exposures in New Homes ...................................................... 37 Policies for Reducing Near-Road Exposures in New Homes ........................................................ 40 Discussion .................................................................................................................................. 48 Chapter Three: Reducing Exposure to Outdoor Particulate Matter in Existing Homes ............................. 50 Part I: High-Efficiency Filtration and Other Measures for Reducing Exposures in Existing Homes ....... 51 High-Efficiency Filtration in Existing Homes ................................................................................ 51 Filtration and other Practices for Reducing Indoor Exposures during Wildfire Smoke Events ...... 53 Discussion .................................................................................................................................. 56 Part II: Strengthening Policies for Reducing Exposures in Existing Homes .......................................... 58 Housing Codes: Strengthening Minimum Property Maintenance Standards ............................... 59 Landlord-Tenant Laws ................................................................................................................ 63 Other Laws Addressing Indoor Environmental Conditions in Existing Homes .............................. 64 Discussion .................................................................................................................................. 65 Part III: Providing Funding for Reducing Exposures in Existing Homes ................................................ 70 Funding for Energy Retrofits and Housing Repairs ...................................................................... 70 Funding to Reduce Wildfire Smoke Exposures ............................................................................ 78 Discussion .................................................................................................................................. 83 Executive Summary Particle Pollution is an Important Public Health Issue in the United States Communities throughout the United States are affected by ambient air pollution from a variety of sources, including industrial facilities and power plants, cars and trucks, wildfires, and residential wood burning. One of the most significant air pollutants in terms of health risks is particulate matter (PM) – a mixture of small, solid particles and liquid droplets that may be emitted from a source directly or formed in the atmosphere as a result of complex reactions of other chemicals. Once inhaled, some of these particles can pass the nasal defenses, penetrate deep into the lungs, and even enter the bloodstream. The health effects from exposure to particulate matter – especially fine particles, or PM2.5 – have been studied for years, and scientific evidence of the risks continues to mount. Exposure to particle pollution is associated with a range of respiratory and cardiovascular symptoms and diseases, as well as premature death. Older adults, children, and people with heart or lung diseases are especially vulnerable to the harmful effects of breathing particulate matter. The U.S. has achieved substantial progress in reducing ambient air pollution over the past several decades, thanks in large measure to passage and implementation of the federal Clean Air Act. Nonetheless, research has found that harmful health effects can occur at PM levels below the limits set by federal law, and no threshold value has been identified. Moreover, many communities are impacted by pollution from local sources, such as high-volume roads, which may not be reflected in state and local air monitoring. While areas throughout the country are affected by particle pollution, studies have documented disproportionate air pollution exposures in communities of color and low-income communities. A key to improving public health and mitigating climate change is to reduce air pollution at the source, e.g., by transitioning to cleaner power and cleaner vehicles. In the meantime, millions of people will continue to be at risk of serious health effects from particle pollution. As we work toward a future of greatly reduced emissions, action is needed now to minimize exposures. The large majority of PM exposures in the U.S. occur indoors, where people spend most of their time. States, tribes, and local governments have an important role to play in advancing building design, construction, operation, and maintenance practices that reduce indoor exposure to outdoor particle pollution. This report highlights opportunities for developing policies and programs that can help improve public health and increase the resilience and adaptive capacity of individuals and buildings in the years ahead. Well-Established Building Practices can Reduce Indoor Exposure to Outdoor Particle Pollution Particles in outdoor air enter buildings through cracks and gaps in the building envelope and through natural or mechanical ventilation. Fortunately, building science provides solutions that can help reduce indoor exposure to outdoor pollutants by: Reducing infiltration of outdoor air – e.g., through sealing of the building envelope, important for reducing entry of outdoor pollutants and also a central strategy for improving energy efficiency; i Environmental Law Institute Providing adequate outside air for ventilation – important for avoiding the buildup of pollutants from indoor sources that can occur with a tight building envelope; and Ensuring adequate air filtration – important for filtering pollutants when outside air is brought in through ventilation systems and when air recirculates within the building. Building design and construction practices for applying these principles to reduce indoor PM exposures are well established and readily available. In particular, there is now broad consensus among building science experts that high-efficiency filtration can be very effective at removing particles indoors. New and renovated mechanical systems can be designed to accommodate high-efficiency filters, facilitate regular filter replacement, and run efficiently to help minimize the cost of operating the system. Existing homes vary widely in the protection they provide against outdoor particle pollution. In situations where it is not possible to provide higher-efficiency filters in a home’s mechanical system, portable air
Recommended publications
  • Trans-Boundary Haze Pollution in Southeast Asia: Sustainability Through Plural Environmental Governance
    sustainability Article Trans-Boundary Haze Pollution in Southeast Asia: Sustainability through Plural Environmental Governance Md Saidul Islam 1,*, Yap Hui Pei 2 and Shrutika Mangharam 1 1 Division of Sociology, Nanyang Technological University, 14 Nanyang Drive, Singapore 637332; [email protected] 2 Division of Psychology, Nanyang Technological University, 14 Nanyang Drive, Singapore 637332; [email protected] * Correspondence: [email protected]; Tel.: +65-6592-1519 Academic Editor: Marc A. Rosen Received: 29 February 2016; Accepted: 13 May 2016; Published: 21 May 2016 Abstract: Recurrent haze in Southeast Asian countries including Singapore is largely attributable to rampant forest fires in Indonesia due to, for example, extensive slash-and-burn (S & B) culture. Drawing on the “treadmill of production” and environmental governance approach, we examine causes and consequences of this culture. We found that, despite some perceived benefits, its environmental consequences include deforestation, soil erosion and degradation, global warming, threats to biodiversity, and trans-boundary haze pollution, while the societal consequences comprise regional tension, health risks, economic and productivity losses, as well as food insecurity. We propose sustainability through a plural coexistence framework of governance for targeting S & B that incorporates strategies of incentives, education and community resource management. Keywords: slash-and-burn; environmental governance; haze; Indonesia; plural coexistence; global warming; Singapore 1. Introduction The world’s rapidly growing population has been a long-standing cause of concern amongst both economists and environmentalists alike. There is an increasing demand for agricultural and urban spaces to sustain the ever-multiplying demographics. However, due to limited availability of space, the trend of clearing forests to make way for cultivable land has been gaining popularity [1].
    [Show full text]
  • Acute Health Impacts of the Southeast Asian Transboundary Haze Problem—A Review
    International Journal of Environmental Research and Public Health Review Acute Health Impacts of the Southeast Asian Transboundary Haze Problem—A Review Kang Hao Cheong 1,* , Nicholas Jinghao Ngiam 2 , Geoffrey G. Morgan 3, Pin Pin Pek 4,5, Benjamin Yong-Qiang Tan 2, Joel Weijia Lai 1, Jin Ming Koh 1, Marcus Eng Hock Ong 4,5 and Andrew Fu Wah Ho 6,7,8 1 Science and Math Cluster, Singapore University of Technology and Design, Singapore 487372, Singapore 2 Division of Neurology, Department of Medicine, National University Health System, Singapore 119074, Singapore 3 School of Public Health, The University of Sydney, Sydney, NSW 2006, Australia 4 Department of Emergency Medicine, Singapore General Hospital, Singapore 169608, Singapore 5 Health Services & Systems Research, Duke-NUS Medical School, Singapore 169857, Singapore 6 SingHealth Duke-NUS Emergency Medicine Academic Clinical Programme, Singapore 169857, Singapore 7 National Heart Research Institute Singapore, National Heart Centre, Singapore 169609, Singapore 8 Cardiovascular & Metabolic Disorders Programme, Duke-NUS Medical School, Singapore 169857, Singapore * Correspondence: [email protected] Received: 20 August 2019; Accepted: 29 August 2019; Published: 6 September 2019 Abstract: Air pollution has emerged as one of the world’s largest environmental health threats, with various studies demonstrating associations between exposure to air pollution and respiratory and cardiovascular diseases. Regional air quality in Southeast Asia has been seasonally affected by the transboundary haze problem, which has often been the result of forest fires from “slash-and-burn” farming methods. In light of growing public health concerns, recent studies have begun to examine the health effects of this seasonal haze problem in Southeast Asia.
    [Show full text]
  • The Criteria Pollutants & a Closer Look at Ozone
    Module 1: Activity 4 The Criteria Pollutants & a Closer Look at Ozone SUMMARY Students will be introduced to the criteria pollutants and will work in groups to make cartoon booklets demonstrating the formation of ground-level ozone and the destruction of stratospheric ozone. ESSENTIAL QUESTIONS • What are criteria pollutants and why are they of concern? • What’s the difference between stratospheric ozone and ground-level ozone? • Why do we sometimes have too much ozone in the troposphere and not enough in the stratosphere? • How do these problems affect human health? TIME NEEDED Highly variable. It’s possible to complete this activity in one block period if you just use the background information provided and have students create a comic strip individually. However if you want to give students more time to produce creative products, allow two full days to work on the project in groups, and 30 minutes to present projects in class. 2012 North Carolina ESSENTIAL STANDARDS FOR EARTH/ENVIRONMENTAL SCIENCE • EEn.2.5.1 Summarize the structure and composition of our atmosphere. • EEn.2.5.5 Explain how human activities affect air quality. • EEn.2.7.3 Explain how human activities impact the biosphere. A product of the NC Air Awareness Program 2014. Available for re-distribution with permission. [email protected] www.itsourair.org The Criteria Pollutants & Module 1: a Closer Look at Ozone Activity 4 (usually over 75° F). NOX comes from burning fuels. VOCs are MAKING chemicals containing carbon that evaporate easily – which usually means they are smelly. Sources of VOCs include CONNECTIONS cleaning chemicals, solvents, paints, unburned gasoline, hog In this activity, students will be learning about ozone waste lagoons, and natural sources such as trees.
    [Show full text]
  • Climate Change, Indoor Air Quality and Health
    CLIMATE CHANGE, INDOOR AIR QUALITY AND HEALTH Prepared for U.S. Environmental Protection Agency Office of Radiation and Indoor Air August 24, 2010 By Paula Schenck, MPH A. Karim Ahmed, PhD Anne Bracker, MPH, CIH Robert DeBernardo, MD, MBA, MPH Section of Occupational and Environmental Medicine Center for Indoor Environments and Health Climate Change, Indoor Air Quality and Health By Paula Schenck, MPH A. Karim Ahmed, PhD Anne Bracker, MPH CIH Robert DeBernardo MD MBA MPH University of Connecticut Health Center Section of Occupational and Environmental Medicine Center for Indoor Environments and Health 1. Introduction and problem statement ......................................................................................1 Background .........................................................................................................................1 2. Climate change and health as relates to indoor environment ...............................................3 National Institute of Environmental Health Science 2010 report........................................3 3. Environment and agents of concern in the indoor environment ..........................................4 Temperature ........................................................................................................................4 Outdoor air contaminants and indoor air quality .................................................................4 Components of indoor air, links with adaptation measures and climate change.................4 4. “Green buildings”, indoor
    [Show full text]
  • Smoke Episodes and Assessment of Health Impacts Related to Haze from Forest Fires: Indonesian Experience
    Health Guidelines for Vegetation Fire Events, Lima, Peru, 6-9 October 1998. Background papers © WHO, 1999 SMOKE EPISODES AND ASSESSMENT OF HEALTH IMPACTS RELATED TO HAZE FROM FOREST FIRES: INDONESIAN EXPERIENCE Yudanarso Dawud The Indonesian Association of Pulmonologists Persahabatan Hospital Jalan Raya Persahabatan Jakarta Timur 13230 Indonesia INTRODUCTION Uncontrolled forest fire in Indonesia has caused smoke pollution in the country as well as other countries in this particular part of the world. The haze episodes in the Southeast Asian region constituted a substantial health risk to the public in 1997 and early 1998 This was evidenced by widespread increases of health-related ambient air quality standards and guidelines for particulate matter. In 1997, in relation to clinical indicators of health, this risk was reflected in increased respiratory-related hospital visits in the most heavily impacted areas during the peak period of the haze. Forest fires have been occuring almost yearly, especially during the dry season, at certain locations in Indonesia including Kalimantan, Sumatera, Java, Sulawesi, Maluku and Irian Jaya. From July to the beginning of October 1997, smoke haze from uncontrolled forest fires had spread throughout some neighbouring countries such as Brunei Darussalam, Malaysia, Southern Philippines, Singapore and Southern Thailand. The Coordinator Minister of Social Welfare of Indonesia declared these uncontrolled forest fires, especially in Sumatera and Kalimantan, as national disaster. 313 Health Guidelines for Vegetation Fire Events, Lima, Peru, 6-9 October 1998. Background papers © WHO, 1999 In a WHO meeting on the health impacts of haze in June 1998, it was mentioned that the severity and extent of the smoke haze pollution were unprecedented, affecting an area with a population of 300 million people across the region.
    [Show full text]
  • Focus on Sulfur Dioxide (SO2)
    The information presented here reflects EPA's modeling of the Clear Skies Act of 2002. The Agency is in the process of updating this information to reflect modifications included in the Clear Skies Act of 2003. The revised information will be posted on the Agency's Clear Skies Web site (www.epa.gov/clearskies) as soon as possible. Overview of the Human Health and Environmental Effects of Power Generation: Focus on Sulfur Dioxide (SO2), Nitrogen Oxides (NOX) and Mercury (Hg) June 2002 Contents The Clear Skies Initiative is intended to reduce the health and environmental impacts of power generation. This document briefly summarizes the health and environmental effects of power generation, specifically those associated with sulfur dioxide (SO2), nitrogen oxides (NOX), and mercury (Hg). This document does not address the specific impacts of the Clear Skies Initiative. • Overview -- Emissions and transport • Fine Particles • Ozone (Smog) • Visibility • Acid Rain • Nitrogen Deposition • Mercury Photo Credits: 1: USDA; EPA; EPA; VTWeb.com 2: NADP 6: EPA 7: ?? 10: EPA 2 Electric Power Generation: Major Source of Emissions 2000 Sulfur Dioxide 2000 Nitrogen Oxides 1999 Mercury Fuel Combustion- Industrial Processing electric utilities Transportation Other stationary combustion * Miscellaneous * Other stationary combustion includes residential and commercial sources. • Power generation continues to be an important source of these major pollutants. • Power generation contributes 63% of SO2, 22% of NOX, and 37% of man-made mercury to the environment. 3 Overview of SO2, NOX, and Mercury Emissions, Transport, and Transformation • When emitted into the atmosphere, sulfur dioxide, nitrogen oxides, and mercury undergo chemical reactions to form compounds that can travel long distances.
    [Show full text]
  • Severe Haze in Northern China: a Synergy of Anthropogenic Emissions and Atmospheric Processes INAUGURAL ARTICLE
    Severe haze in northern China: A synergy of anthropogenic emissions and atmospheric processes INAUGURAL ARTICLE Zhisheng Ana,b,c,d,e,1, Ru-Jin Huanga,b,c,d,e, Renyi Zhangf,g, Xuexi Tiea,c, Guohui Lia,b,c,h, Junji Caoa,b,c,h, Weijian Zhoua,b,d,e, Zhengguo Shia,b,h, Yongming Hana,b,c,h, Zhaolin Guh, and Yuemeng Jif,i aState Key Laboratory of Loess and Quaternary Geology, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China; bCenter for Excellence in Quaternary Science and Global Change, Chinese Academy of Sciences, Xi’an 710061, China; cKey Laboratory of Aerosol Chemistry and Physics, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China; dInterdisciplinary Research Center of Earth Science Frontier, Beijing Normal University, Beijing 100875, China; eOpen Studio for Oceanic-Continental Climate and Environment Changes, Pilot National Laboratory for Marine Science and Technology (Qingdao), Qingdao 266061, China; fDepartment of Atmospheric Sciences, Texas A&M University, College Station, TX 77843; gDepartment of Chemistry, Texas A&M University, College Station, TX 77843; hDepartment of Earth and Environmental Sciences, Xi’an Jiaotong University, Xi’an 710049, China; and iGuangzhou Key Laboratory of Environmental Catalysis and Pollution Control, School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006, China This contribution is part of the special series of Inaugural Articles by members of the National Academy of Sciences elected in 2016. Contributed by Zhisheng An, March 14, 2019 (sent for review January 4, 2019; reviewed by Qiang Fu and Jianping Huang) Regional severe haze represents an enormous environmental documented by large fractions and high abundances of secondary problem in China, influencing air quality, human health, ecosys- organic aerosol (SOA) and secondary inorganic aerosol (SIA) tem, weather, and climate.
    [Show full text]
  • Technical Assistance Document for the Reporting of Daily Air Quality – the Air Quality Index (AQI)
    Technical Assistance Document for the Reporting of Daily Air Quality – the Air Quality Index (AQI) EPA 454/B-18-007 September 2018 Technical Assistance Document for the Reporting of Daily Air Quality – the Air Quality Index (AQI) U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Air Quality Assessment Division Research Triangle Park, NC CONTENTS I. REPORTING THE AQI II. CALCULATING THE AQI III. FREQUENTLY ASKED QUESTIONS IV. RESOURCES LIST OF TABLES Table 1. Names and colors for the six AQI categories Table 2. AQI color formulas Table 3. Pollutant-Specific Sensitive Groups Table 4. Cautionary Statements Table 5. Breakpoints for the AQI LIST OF FIGURES Figure 1. The AQI is reported in many formats Figure 2. Display of AQI forecast Figure 3. The NowCast Figure 4. Airnow.gov page showing the AQI at U.S. Embassies and Consulates Figure 5. The AQI on AirNow’s Fires: Current Conditions page Figure 6. The AirNow widget This guidance is designed to aid local agencies in reporting air quality using the Air Quality Index (AQI) as required in 40 CFR Part 58.50 and according to 40 CFR Appendix G to Part 58. I. REPORTING THE AQI Do I have to report the AQI? Metropolitan Statistical Areas (MSAs) with a population of more than 350,000 are required to report the AQI daily to the general public. The population of an MSA for purposes of index reporting is based on the latest available U.S. census population. How often do I report the AQI? MSAs must report the AQI daily, which is defined as at least five days each week.
    [Show full text]
  • A Review on Air Quality Indexing System
    Asian Journal of Atmospheric Environment Vol. 9-2, pp. 101-113, June 2015 Ozone Concentration in the Morning in InlandISSN(Online) Kanto Region 2287-1160 101 doi: http://dx.doi.org/10.5572/ajae.2015.9.2.101 ISSN(Print) 1976-6912 A Review on Air Quality Indexing System Kanchan, Amit Kumar Gorai1),* and Pramila Goyal2) Department of Civil and Environmental Engineering, Birla Institute of Technology, Mesra, Ranchi­835215, India 1)Department of Mining Engineering, National Institute of Technology, Rourkela, Odisha­769008, India 2)Centre for Atmospheric Sciences, Indian Institute of Technology, Delhi, Delhi­110016, India *Corresponding author. Tel: +91­661­2462938, E­mail: [email protected] Globally, many cities continuously assess air quality ABSTRACT using monitoring networks designed to measure and record air pollutant concentrations at several points Air quality index (AQI) or air pollution index (API) is deemed to represent exposure of the population to commonly used to report the level of severity of air these pollutants. Current research indicates that guide­ pollution to public. A number of methods were dev­ eloped in the past by various researchers/environ­ lines of recommended pollution values cannot be regar­ mental agencies for determination of AQI or API but ded as threshold values below which a zero adverse there is no universally accepted method exists, which response may be expected. Therefore, the simplistic is appropriate for all situations. Different method comparison of observed values against guidelines may uses different aggregation function in calculating mislead unless suitably quantified. In recent years, air AQI or API and also considers different types and quality information are provided by governments to the numbers of pollutants.
    [Show full text]
  • Transboundary Haze Pollution Problem in Southeast Asia: Reframing ASEAN’S Response
    ERIA-DP-2015-82 ERIA Discussion Paper Series Transboundary Haze Pollution Problem in Southeast Asia: Reframing ASEAN’s Response Apichai SUNCHINDAH Policy Adviser/Development Specialist December 2015 Abstract: ASEAN has experienced periodic episodes of transboundary haze pollution resulting from land and forest fires caused by seasonal burning to clear vegetation on the ground for various purposes. Some of these incidents were severe like in mid- 2013 and 2015 for parts of Indonesia, Malaysia, Singapore, and Thailand as well as in early 2015 for portions of Lao PDR, Myanmar, and Thailand. Despite more than a decade since the ASEAN Haze Agreement came into force, the problem still recurs and sometimes with serious consequences to health, transportation, tourism, and other activities. What is urgently needed is a reframing of the way the issue is being currently addressed, i.e. mostly tackling at the tail-end of the problem of putting out the fires after they have been lit rather than preventing or curbing the illegal burning practices at source. It also represents balancing economic development initiatives with environmental protection and international relations concerns. Keyword: Keywords: ASEAN, transboundary haze pollution, reframing 1. Transboundary Haze Pollution and ASEAN’s Response Transboundary haze pollution has been a recurrent phenomenon in the ASEAN region to various degrees over the years. These incidences have arisen due mainly to the cumulative effect of slash and burn and/or other types of moderate to large-scale burning to clear land for growing agricultural crops like corn and plantation trees such as pulp wood, rubber or oil palm and all of this often occurring concurrently.
    [Show full text]
  • Revised Air Quality Standards for Particle Pollution and Updates to the Air Quality Index (Aqi)
    The National Ambient Air Quality Standards for Particle Pollution REVISED AIR QUALITY STANDARDS FOR PARTICLE POLLUTION AND UPDATES TO THE AIR QUALITY INDEX (AQI) On Dec. 14, 2012 the U.S. Environmental Protection Agency (EPA) strengthened the nation’s air quality standards for fine particle pollution to improve public health protection by revising the 3 primary annual PM2.5 standard to 12 micrograms per cubic meter (µg/m ) and retaining the 24- hour fine particle standard of 35 µg/m3. Exposure to fine particle pollution can cause premature death and harmful cardiovascular effects such as heart attacks and strokes, and is linked to a variety of other significant health problems. Particle pollution also harms public welfare, including causing haze in cities and some of our nation’s most treasured national parks. EPA has issued a number of rules that will make significant strides toward reducing fine particle pollution (PM2.5). These rules will help the vast majority of U.S. counties meet the revised PM2.5 standard without taking additional action to reduce emissions. AIR QUALITY STANDARDS The Clean Air Act requires EPA to set two types of outdoor air quality standards: primary standards, to protect public health, and secondary standards, to protect the public against adverse environmental effects. The law requires that primary standards be “requisite to protect public health with an adequate margin of safety,” including the health of people most at risk from PM exposure. These include people with heart or lung disease, children, older adults and people of lower socioeconomic status. Secondary standards must be “requisite to protect the public welfare” from both known and anticipated adverse effects.
    [Show full text]
  • Acid Rain and Transported Air Pollutants: Implications for Public Policy
    Appendix B Effects of Transported Pollutants B.1 AQUATIC RESOURCES AT RISK (p. 207) B.2 TERRESTRIAL RESOURCES AT RISK (p. 217) B.3 MATERIALS AT RISK (p. 239) B.4 VISIBILITY IMPAIRMENT (p. 244) B.5 HUMAN HEALTH RISKS (p. 255) B.6 ECONOMIC SECTORS AT GREATEST RISK FROM CONTROLLING OR NOT CONTROLLING TRANSPORTED POLLUTANTS (p. 261) B. 1 AQUATIC RESOURCES AT RISK Extent of Resources at Risk* Because of the large area of a typical watershed, most of the acid ultimately deposited in lakes and streams Scientists are concerned that acid deposition may be comes from water that runs off or percolates through damaging substantial numbers of U. S. and Canadian the surrounding land mass, rather than from precipita- lakes and streams. As part of its assessment of trans- tion falling directly on water bodies. The amount of ported air pollutants, OTA contracted with The Insti- acidifying material that actually enters a given lake or tute of Ecology (TIE) to: stream is determined primarily by the soil and geologic ● describe mechanisms by which acid deposit ion conditions of the surrounding watershed. Whcn the two may be affecting sensitive 1akes and streams; major chemical components of’ acid rain-nitric acid and ● providc an inventory of Eastern U.S. lakes and sulfuric acid—reach the ground, they may react with streams considered to be sensitive to acid depo- soils is a variety of ways. * * For example, soils can neu- sit ion; tralize the acids, exchange nutrients and trace metals ● estimate the number of lakes and streams in these for components of the acids, and/or hold sulfuric acid.
    [Show full text]