BRI news stories have appeared in many regional, national, and international news outlets. These stories help promote awareness of our work, but also promote the general issues of conservation biology and the need to continue research in wildlife health and its implications to human health.
BRI's researchers are available to talk to journalists and provide expert information on both their work and the broader topics of their expertise.
For more information, visit our page on Resources for Journalists.
Coal-fired power plants are the largest source of mercury in the U.S., accounting for approximately 48% of mercury emissions in 2015. The Mercury and Air Toxics Standards (MATS) were finalized in 2012 to regulate emissions of mercury, acid gases and other hazardous air pollutants (HAPs) from U.S. electric utilities.
The 2012 MATS rule was intended to reduce mercury emissions from regulated power plants by 90%, improve public health, and help meet U.S. commitments under the 2017 Minamata Convention on Mercury.
On April 16, 2020, the Environmental Protection Agency (EPA) overturned the Agency’s prior determination and deemed that it is not “appropriate and necessary” to regulate mercury and other hazardous air pollutants (HAPs) from oil- and coal-fired power plants under section 112 of the Clean Air Act. According to legal scholars, this decision undermines the foundation of the MATS rule and invites challenges to the emissions standards themselves.
The EPA also issued a “Residual Risk and Technology Review” in which it concluded that no further emissions reductions will be required from affected power plants to protect human health. The EPA Science Advisory Board recently issued a report urging the Agency to develop a new mercury exposure estimate before finalizing this residual risk assessment.
EPA’s justification for weakening MATS relies not only on its decision to eliminate “co-benefits” but also on a flawed underestimation of the benefits of reducing mercury itself. The 2012 MATS rule has substantially decreased mercury emissions and improved public health at a much lower cost than anticipated. Yet, EPA continues to rely on the outdated cost and health benefit estimates from the 2011 MATS Regulatory Impact Assessment (RIA) to support its determination.
EPA’s “appropriate and necessary” and “residual risk” determinations are inconsistent with current science on mercury exposure, the societal impacts of mercury pollution in the U.S.,, and the full benefits of emissions controls. Among other shortcomings, the 2011 MATS RIA that EPA relied on only accounts for the benefits of mercury reductions to children of freshwater recreational anglers in the U.S., a small fraction of the total population affected.
Mercury has been studied intensively for decades and its impacts are well-understood. Important facts about the effects of mercury include the following:
Mercury exposure in the U.S. occurs primarily through the consumption of freshwater fish and seafood (fish and shellfish). The consumption of marine fish, often harvested from U.S. coastal waters, accounts for greater than 80% of methylmercury intake by the U.S. population. Dietary supplements cannot counteract methylmercury toxicity in U.S. consumers. A safe and consumable fishery is important to retaining a healthy, low-cost source of protein and other nutrients that are essential for pregnant women, young children, and the general population.
After mercury is emitted from power plants it is deposited back to Earth where it can be converted to methylmercury, a highly toxic form of mercury that magnifies up food chains, reaching concentrations in fish that are 10 to 100 million times greater than concentrations in water.
With increasing levels of mercury in the environment due to human activities, virtually all fish from U.S. waters now have detectable levels of methylmercury. Some fish, such as swordfish, large species of tuna, and freshwater game fish, can have levels that exceed consumption guidelines.
States post fish consumption advisories for waterbodies that are known to have elevated contaminants. In 2013, consumption advisories for mercury were in effect in all 50 states, one U.S. territory, and three tribal territories, and accounted for 81% of all U.S. consumption advisories. This represents more advisories for mercury than for all other contaminants combined.
Wildlife that consume fish, such as common loons, bald eagles, otter and mink, and many marine mammals can also experience adverse effects from mercury and are unable to heed advisories. The health of many songbird and bat species is threatened due to methylmercury exposure in wetland habitats. The productivity of economically valuable game fish stocks can also be compromised.
The outdated science from the 2011 MATS RIA that EPA relied on in its current decision assumed that mercury emissions from coal-fired utilities are mainly transported long distances from the U.S. and that a substantial fraction of mercury in the U.S. comes from international sources. However, scientific understanding of the fate of U.S. mercury emissions has advanced considerably since 2011,. Recent research shows that the contribution of U.S. coal-fired power plants to local mercury contamination particularly in the eastern U.S. has been markedly underestimated. Accordingly, mercury controls on U.S. electric utilities have contributed to the following emissions reductions and associated environmental and human health improvements in the U.S.
The EPA continues to estimate that the annualized mercury-related health benefits of reducing mercury emissions would be less than $10 million. Recent studies that account for more pathways of methylmercury exposure and additional health effects suggest that the monetized benefits of reducing power plant mercury emissions in the U.S. are likely in the range of several billion dollars per year,,. These and other studies support the conclusion that the mercury-related benefits from MATS are orders of magnitude larger than previously estimated in the 2011 MATS RIA on which the EPA’s decision is based.
In addition to the mercury-related benefits, MATS has also decreased sulfur dioxide and nitrogen oxide emissions, improving air quality and public health by reducing fine particulate matter and ground-level ozone. The EPA estimated that the annualized value of these additional benefits is $24 to $80 billion; bringing the total annual benefits from MATS to tens of billions of dollars. Even with these more complete estimates, substantial benefits of reducing mercury and other air toxics remain unquantified due to data limitations.
On the cost side, new information suggests that the EPA’s original cost-estimate for MATS of $9.6 billion is much higher than the actual cost due to declines in natural gas prices and lower than expected control equipment and renewable energy costs. Yet, even with the original overestimate, the EPA projected that MATS would increase the monthly electric bill of the average American household by only $2.71 (or 0.3 cents per kilowatt-hour). This value is well within the price fluctuation consumers experienced between 2000 and 2011.
The science is clear. Total methylmercury exposure must be taken into account in policy decisions. The health impacts in the U.S. of mercury emissions in the U.S. are large and disproportionately affect children and other vulnerable populations. Mercury emission standards in the U.S. have markedly reduced mercury in the environment and improved public health. The mercury-related benefits alone of the MATS rule are much larger than EPA has estimated, the actual costs appear to be substantially lower than EPA has projected, and the total monetized benefits across all pollutants far outweigh the cost of the standards.
Charles Driscoll, Department of Civil and Environmental Engineering, Syracuse University
Elsie Sunderland, Harvard Paulson School of Engineering & Applied Sciences and Harvard T.H. Chan School of Public Health, Department of Environmental Health, Exposure, Epidemiology and Risk
Kathy Fallon Lambert, Harvard T.H. Chan School of Public Health, Center for Climate, Health, and the Global Environment
Joel Blum, Department of Earth and Environmental Sciences, University of Michigan
Celia Chen, Department of Biological Sciences, Dartmouth College
David Evers, Biodiversity Research Institute
Philippe Grandjean, Harvard T.H. Chan School of Public Health, Department of Environmental Health, Environmental and Occupational Medicine and Epidemiology
Rob Mason, Departments of Chemistry and Marine Sciences, University of Connecticut
Emily Oken, Harvard Medical School
Noelle Selin, Institute for Data, Systems, and Society and Department of Earth, Atmospheric and Planetary Sciences, Massachusetts Institute of Technology
 Streets, D.G.; Horowitz, H.M.; Lu, Z.; Levin, L.; Thackray, C.P.; Sunderland, E.M. 2019. Global and regional trends in mercury emissions and concentrations, 2010-2015. Atmospheric Environment. 201, 417-427. doi.org/10.1016/j.atmosenv.2018.12.031.
 Sunderland, E.M.; Driscoll, Jr., C.T.; Hammitt, J.K.; Grandjean, P.; Evans, J.S.; Blum, J.D.; Chen, C.Y.; Evers, D.C.; Jaffe, D.A.; Mason, R.P.; Goho, S.; Jacobs, W. 2016. Benefits of Regulating Hazardous Air Pollutants from Coal and Oil-Fired Utilities in the United States. Environmental Science & Technology. 50 (5), 2117-2120. DOI: 10.1021/acs.est.6b00239.
 Giang, A.; Mulvaney, K; Selin, N.E. 2016. Comments on “Supplemental Finding That It Is Appropriate and Necessary to Regulate Hazardous Air Pollutants from Coal- and Oil-Fired Electric Utility Steam Generating Units”.
 Grandjean, P. and Bellanger, M. 2017. Calculation of the disease burden associated with environmental chemical exposures: application of toxicological in health economic estimation. 16:123. DOI: 10.1186/s12940-017-0340-3.
 Genchi G., Sinicropi M.S., Carocci A., Lauria G., Catalano A. 2017. Mercury Exposure and Heart Diseases. Int J Environ Res Public Health. 2017;14(1):74. Published Jan 12. DOI:10.3390/ijerph14010074.
 Tan, S.W.; Meiller, J.C.; Mahaffey, K.R. 2009. The endocrine effects of mercury in humans and wildlife. Crit. Rev. Toxicol. 39 (3), 228−269.
 He, K.; Xun, P.; Liu, K.; Morris, S.; Reis, J.; Guallar, E. 2013. Mercury exposure in young adulthood and incidence of diabetes later in life: the CARDIA trace element study. Diabetes Care. 36, 1584−1589.
 Nyland, J. F.; Fillion, M.; Barbosa, R., Jr.; Shirley, D. L.; Chine, C.; Lemire, M.; Mergler, D.; Silbergeld, E.K. 2011. Biomarkers of methylmercury exposure and immunotoxicity among fish consumers in the Amazonian Brazil. Env. Health Persp. 119 (12), 1733− 1738.
 Rice, G.E.; Hammitt, J.K; and Evans, J.S. 2010. A probabilistic characterization of the health benefits of reducing methyl mercury intake in the United States. Environ Sci Technol. 1;44(13):516-24. DOI:10.1021/es903359u.
 Sunderland, E. M.; Li, M.; Bullard, K. 2018. Decadal Changes in the Edible Supply of Seafood and Methylmercury Exposure in the United States. Environ. Health Persp. DOI: 10.1289/EHP2644.
 Driscoll, C.T.; Han, Y-J; Chen, C.; Evers, D.; Lambert, K.F.; Holsen, T.; Kamman, N.; and Munson, R. 2007. Mercury Contamination on Remote Forest and Aquatic Ecosystems in the Northeastern U.S.: Sources, Transformations, and Management Options. BioScience. 57(1):17-28.
 U.S. Environmental Protection Agency. 2011 National Listing of Fish Advisories. 2013. EPA-820-F-13-058.
 Chan, N.M.; Scheuhammer, A.M.; Ferran, A.; Loupelle, C.; Holloway, J.; and Weech, S. 2003. Impacts of Mercury on Freshwater Fish-eating Wildlife and Humans. Human and Ecological Risk Assessment. 9(4): 867-883.
 Sandheinrich, M.B.; Wiener, J.G. 2011. Methylmercury in freshwater ﬁsh: Recent advances in assessing toxicity of environmentally relevant exposures. In Environmental Contaminants in Biota: Interpreting Tissue Concentrations, 2nd; Beyer, W. N., Meador, J. P., Eds.; CRC Press/Taylor and Francis: Boca Raton, FL; pp. 169−190.
 Zhang, Y.; Jacob, D.; Horowitz, H.; Chen, L.; Amos, H.; Krabbenhoft, D.; Slemr, F.; St. Louis, V.; Sunderland, E. 2016. Observed decrease in atmospheric mercury explained by global decline in anthropogenic emissions. PNAS. 113 (3) 526-531. DOI: 10.1073/pnas.1516312113.
 Lepak, R.F.; Yin, R.; Krabbenhoft, D.; Ogorek, J.; DeWild, J.; Holsen, T.; and Hurley, J. 2015. Use of Stable Isotope Signatures to Determine Mercury Sources in the Great Lakes. Environmental Science & Technology Letters. 2 (12), 335-34. DOI: 10.1021/acs.estlett.5b00277.
 U.S. Environmental Protection Agency. 2018. https://www.epa.gov/trinationalanalysis/electric-utilities-mercury-releases-2016-tri-national-analysis.
 Cross, F.A.; Evans, D.W.; Barber, R.T. 2015. Decadal declines of mercury in adult bluefish (1972−2011) from the mid-Atlantic coast of the U.S.A. Environ. Sci. Technol. 49, 9064−9072.
 U.S. Environmental Protection Agency. 2013. Trends in Blood Mercury Concentrations and Fish Consumption Among U.S. Women of Childbearing Age NHANES 1999-2010. EPA-823-R-13-002. https://www.regulations.gov/document?D=EPA-HQ-OAR-2009-0234-20544.
 U.S. Environmental Protection Agency. 2013. EPA-823-R-13-002.
 Rice et al. 2010.
 Giang, A.; Selin, N. E. Benefits of mercury controls for the United States. Proc. Natl. Acad. Sci. U. S. A. 2016, 113, 286.
 Sunderland et al. 2016.
 Giang et al. 2016.
 Declaration of James E. Staudt, Ph.D. CFA, September 24, 2015, White Stallion Energy Center, et al., v. United States Environmental Protection Agency, Case No. 12-1100 and Summary plus cases, Exhibit 1 Declaration of James E. Staudt, Ph.D., CFA, U.S. Court of Appeals for the District of Columbia.
 U.S. Environmental Protection Agency. Final Consideration of Cost in the Appropriate and Necessary Finding for the Mercury and Air Toxics Standards for Power Plants. https://www.epa.gov/sites/production/files/2016-05/documents/20160414_mats_ff_fr_fs.pdf.
© 2020 Biodiversity Research Institute is a 501(c)3 non-profit