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Commentary |

Cap and Trade Legislation for Greenhouse Gas Emissions: Title and subTitle BreakPublic Health Benefits From Air Pollution Mitigation

Christopher D. Barr, PhD; Francesca Dominici, PhD
[+] Author Affiliations

Author Affiliations: Department of Biostatistics, Harvard School of Public Health, Boston, Massachusetts.


JAMA. 2010;303(1):69-70. doi:10.1001/jama.2009.1955
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Legislation to cap and trade greenhouse gas emissions was approved by a 219-212 vote of the US House of Representatives on June 26, 20091 (counterpart legislation passed through the Environment and Public Works Committee in the Senate on November 5, 2009). Cap and trade policy articulated in the American Clean Energy and Security (ACES) Act of 20091 regulates greenhouse gases, including carbon dioxide, methane, nitrous oxide, sulfur hexafluoride, hydrofluorocarbons, perfluorocarbons, and nitrogen trifluoride. Debate over the ACES Act focused heavily on economic issues contrasted against concerns about climate change.2 However, discussion largely ignored the potential for cap and trade legislation to contribute to reductions in levels of other harmful air pollutants, such as sulfur dioxide, particulate matter, and ozone precursors, which share emission sources with greenhouse gases.

Under the bill, domestic greenhouse gas emissions are to be capped at 2005 annual levels and reduced to 17% of those marks by 2050.1 The bill provides for an initial round of pollution permits to be made available, some free, others at auction. Subsequently, these permits can be bought and sold in the open market by organizations such as utility companies and manufacturing firms. A key provision in the ACES Act requires the president to impose tariffs on countries that do not implement similar regulations on greenhouse gas emissions. Although other potentially viable legislation such as a tax on carbon emissions has been proposed,3 the current cap and trade legislation is the first bill to pass in either the House of Representatives or the Senate.

The greenhouse gases regulated under the ACES Act do not generally pose serious direct health risks. For example, nitrous oxide is used in dental procedures and carbon dioxide is an ingredient in carbonated beverages. Other greenhouse gases, such as nitrogen trifluoride and sulfur hexafluoride, are not harmful at their current concentration levels but can be hazardous to persons working with them if safety precautions are not taken.

Instead, substantial human health benefits from cap and trade legislation potentially could come from reductions in ambient levels of harmful pollutants, such as particulate matter and ozone, that share emissions sources with greenhouse gases. For example, 94% of carbon dioxide emissions in the United States result from combustion of fossil fuels, with electricity generation and transportation alone comprising nearly 70%. These are also the leading source of sulfur dioxide, fine particles having diameter smaller than 2.5 μm (PM2.5), and precursors to ozone such as mono-nitrogen oxides.4

Although the time scale for potential effects of cap and trade legislation on climate change and related health benefits is likely decades or centuries, ancillary air pollution mitigation could have immediate health benefits. In 2 nationwide epidemiological studies, daily levels of ambient ozone and PM2.5 have been linked to increased risk of cardiovascular and respiratory mortality5 and to increased risk of emergency hospital admissions, especially for heart failure,6 respectively. Estimates of the potential health benefits attributable to reductions in harmful air pollutants resulting from mitigation of greenhouse gas emissions at the city, regional, and national level have been substantial.7

Even though US cap and trade legislation would likely reduce domestic air pollution levels, 2 caveats deserve consideration. First, methods for reducing greenhouse gas emissions typically reduce air pollution levels, but not always. This problem can be highlighted using airplanes as an example.8 Two methods to reduce carbon dioxide emissions from airplanes are to decrease aircraft weight or increase engine combustion temperatures. The former reduces both greenhouse gas and air pollution emissions, whereas the latter reduces greenhouse gas emissions at the cost of increasing precursors to ozone. In the broader context of energy production, it is likely cap and trade legislation would drive a shift away from fossil fuel combustion to sources such as solar technology that produce much less air pollution. However, the exact technology development path is still uncertain.

A second problem is the potential for domestic cap and trade legislation to transfer US emissions to newly industrialized nations. Countries facing lower production costs associated with looser regulations on greenhouse gas emissions would have an economic advantage over manufacturing industries in the United States. However, increased air pollution from new manufacturing could be a key public health issue for developing regions, such as China's Pearl River delta, where air pollution levels are already much higher than standards in the United States.9

The economic and physical systems that would be affected by cap and trade legislation are extremely complex and effects on air pollution will have to be considered in a broad context. For example, although the absence of tariffs would likely push manufacturing, air pollution, and related negative health effects to developing regions, those regions might experience health benefits associated with increased per capita income. The discussion is similarly complex in the physical domain. For example, some air pollutants, such as sulfate particulate matter, can contribute to short-term climate cooling. Although still somewhat unclear, there is an emerging debate over the possibility that air pollution mitigation could actually exacerbate global warming in the short term.10

Although this legislation faces potentially significant opposition and alteration in the Senate, the cap and trade bill recently passed in the House of Representatives has progressed further through Congress than any other similar legislation. There is potential for regulation of greenhouse gas emissions, via cap and trade legislation or other strategies, to simultaneously decrease emissions of harmful air pollutants and reduce morbidity and mortality attributable to cardiovascular and respiratory illness. Such improvements in public health have been linked to economic benefits from recovered workforce productivity8 and add important support for cap and trade legislation.

AUTHOR INFORMATION

Corresponding Author: Christopher D. Barr, PhD, Department of Biostatistics, Harvard School of Public Health, 655 Huntington Ave, Bldg 2, Room 435A, Boston, MA 02115 (cdbarr@gmail.com).

Financial Disclosures: None reported.

Funding/Support: This work was funded by grants RD-83241701 and RD-836622 from the US Environmental Protection Agency.

Role of the Sponsor: The US Environmental Protection Agency had no role in the preparation, review, or approval of the manuscript.

Disclaimer: Although the research described in this article has been funded wholly or in part by the US Environmental Protection Agency through grant agreement RD-83241701 to Johns Hopkins University, it has not been subjected to the Agency's required peer and policy review and therefore does not necessarily reflect the views of the Agency and no official endorsement should be inferred.

Additional Contributions: Michelle L. Bell, PhD (Yale University, New Haven, Connecticut), and David M. Diez, MS (University of California, Los Angeles), provided valuable contributions to the manuscript. Neither of these individuals received extra compensation for their contributions.

 The American Clean Energy and Security Act (HR 2454): section by section summary. http://energycommerce.house.gov/Press_111/20090720/hr2454_sectionsummary.pdf. Accessed November 17, 2009
Broder JM. With something for everyone, climate bill passed. New York Times. June 30, 2009. http://www.nytimes.com/2009/07/01/us/politics/01climate.html. Accessed November 17, 2009
Paltsev S, Reilly JM, Jacoby HD,  et al.  Assessment of US cap-and-trade proposals.  Climate Policy. 2008;8(4):395-420
CrossRef
 2009 US Greenhouse Gas Inventory Report: Executive Summary. http://epa.gov/climatechange/emissions/downloads09/ExecutiveSummary.pdf. Accessed November 17, 2009
Bell ML, McDermott A, Zeger SL, Samet JM, Dominici F. Ozone and short-term mortality in 95 US urban communities, 1987-2000.  JAMA. 2004;292(19):2372-2378
PubMedCrossRef
Dominici F, Peng RD, Bell ML,  et al.  Fine particulate air pollution and hospital admission for cardiovascular and respiratory diseases.  JAMA. 2006;295(10):1127-1134
PubMedCrossRef
Cifuentes L, Borja-Aburto VH, Gouveia N, Thurston G, Davis DL. Hidden health benefits of greenhouse gas mitigation.  Science. 2001;293(5533):1257-1259
PubMedCrossRef
Bell ML, Davis DD, Cifuentes LA, Krupnick AJ, Morgenstern RD, Thurston GD. Ancillary human health benefits of improved air quality resulting from climate change mitigation.  Environ Health. 2008;741
PubMedCrossRef
Streets DG, Yu C, Bergin MH, Wang X, Carmichael GR. Modeling study of air pollution due to the manufacture of export goods in China's Pearl River delta.  Environ Sci Technol. 2006;40(7):2099-2107
PubMedCrossRef
Arneth A, Unger N, Kulmala M, Andreae MO. Atmospheric science: clean the air, heat the planet?  Science. 2009;326(5953):672-673
PubMedCrossRef

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Country-Specific Mortality and Growth Failure in Infancy and Yound Children and Association With Material Stature

Use interactive graphics and maps to view and sort country-specific infant and early dhildhood mortality and growth failure data and their association with maternal

 The American Clean Energy and Security Act (HR 2454): section by section summary. http://energycommerce.house.gov/Press_111/20090720/hr2454_sectionsummary.pdf. Accessed November 17, 2009
Broder JM. With something for everyone, climate bill passed. New York Times. June 30, 2009. http://www.nytimes.com/2009/07/01/us/politics/01climate.html. Accessed November 17, 2009
Paltsev S, Reilly JM, Jacoby HD,  et al.  Assessment of US cap-and-trade proposals.  Climate Policy. 2008;8(4):395-420
CrossRef
 2009 US Greenhouse Gas Inventory Report: Executive Summary. http://epa.gov/climatechange/emissions/downloads09/ExecutiveSummary.pdf. Accessed November 17, 2009
Bell ML, McDermott A, Zeger SL, Samet JM, Dominici F. Ozone and short-term mortality in 95 US urban communities, 1987-2000.  JAMA. 2004;292(19):2372-2378
PubMedCrossRef
Dominici F, Peng RD, Bell ML,  et al.  Fine particulate air pollution and hospital admission for cardiovascular and respiratory diseases.  JAMA. 2006;295(10):1127-1134
PubMedCrossRef
Cifuentes L, Borja-Aburto VH, Gouveia N, Thurston G, Davis DL. Hidden health benefits of greenhouse gas mitigation.  Science. 2001;293(5533):1257-1259
PubMedCrossRef
Bell ML, Davis DD, Cifuentes LA, Krupnick AJ, Morgenstern RD, Thurston GD. Ancillary human health benefits of improved air quality resulting from climate change mitigation.  Environ Health. 2008;741
PubMedCrossRef
Streets DG, Yu C, Bergin MH, Wang X, Carmichael GR. Modeling study of air pollution due to the manufacture of export goods in China's Pearl River delta.  Environ Sci Technol. 2006;40(7):2099-2107
PubMedCrossRef
Arneth A, Unger N, Kulmala M, Andreae MO. Atmospheric science: clean the air, heat the planet?  Science. 2009;326(5953):672-673
PubMedCrossRef
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