Mercury in Context
Coal-fired power plants are the largest source of mercury in the U.S., accounting for approximately 48% of mercury emissions in 2015.1
The Mercury and Air Toxics Standards (MATS) were finalized in 2011 and currently regulate emissions of mercury, acid gases and other hazardous air pollutants (HAPs) from U.S. electric utilities.
The MATS rule is expected to reduce mercury emissions from the power sector by 90%, improve public health, and play an integral role in meeting U.S. commitments under the international 2017 Minamata Convention on Mercury.
The Latest from EPA
In August 2018, the U.S. Environmental Protection Agency (EPA) announced plans to revisit the Agency’s prior determination that regulating HAPs emitted from power plants under section 112 of the Clean Air Act was “appropriate and necessary”.
A proposal to reopen one or more aspects of MATS is currently under interagency review at the Office of Management and Budget and could result in lifting limits on mercury emissions from electric utilities in the U.S.
Recent research shows that MATS has substantially reduced mercury levels in the environment and improved public health at a much lower cost than anticipated. However, the Regulatory Impact Assessment (RIA) that the Administration is relying on in its rollback proposal does not reflect current scientific understanding of the local impacts and societal cost of mercury pollution in the U.S. 2,3
Many of the health effects associated with mercury exposure are not fully reflected in the RIA, and the final estimate of the mercury-related benefits from MATS only accounted for benefits to children of freshwater recreational anglers in the U.S., a small fraction of the total population affected.
Mercury Emissions Matter to Human Health and the Environment
Mercury in the form of methylmercury is a potent neurotoxin. Important facts about the health effects of methylmercury include the following:
- Children exposed to methylmercury during a mother’s pregnancy can experience persistent and lifelong IQ and motor function deficits.4
- In adults, high levels of methylmercury exposure have been associated with adverse cardiovascular effects, including increased risk of fatal heart attacks.5
- Other adverse health effects of methylmercury exposure that have been identified in the scientific literature include endocrine disruption,6 diabetes risk,7 and compromised immune function.8
- The societal costs of neurocognitive deficits associated with methylmercury exposure in the U.S. were estimated in 2017 to be approximately $4.8 billion per year.9
- No known threshold exists for methylmercury below which neurodevelopmental impacts do not occur.10,11
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.12 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.13
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. advisories.14 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.15 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.16
As Mercury Emissions in the U.S. Have Declined, Health Has Improved
In the 2011 MATS RIA, it was assumed that mercury emissions from coal-fired utilities are mainly transported long-distances away from the U.S. and that a substantial fraction of mercury in the U.S. comes from international sources. Since that time, scientific understanding of the fate of U.S. mercury emissions has advanced.17,18 Recent research reveals that the contribution of U.S. coal-fired power plants to local mercury contamination in the U.S. has been markedly underestimated. Accordingly, controls on mercury emissions from U.S. electric utilities have contributed to the following human health and environmental improvements.
- Mercury emissions from U.S. coal-fired power plants have declined by 85% from 92,000 pounds in 2006 to 14,000 pounds in 201619 since states began setting standards and MATS was introduced in 2011. Eleven states had implemented mercury emissions standards for power plants prior to 2011.
- Concurrent with declines in mercury emissions, mercury levels in air, water, sediments, loons, freshwater fisheries, and Atlantic Ocean fisheries20 have decreased appreciably.
- Mercury levels in the blood of women in the U.S. declined by 34% between 2001 and 2010 as mercury levels in some fish decreased, and fish consumption advisories improved.21
- The estimated number of children born in the U.S. each year with prenatal exposure to methylmercury levels that exceed the EPA reference dose has decreased by half from 200,000-400,000 to 100,000-200,000, depending on the measure used.22
The Benefits of Reducing Mercury Are Much Larger Than Previously Estimated
The EPA estimated in the MATS RIA 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.23,24,25 These and other studies support the conclusion that the mercury-related benefits from MATS are orders of magnitude larger than previously estimated in the MATS RIA.26
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.27
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.28 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 2011.29
The Bottom Line
The science is clear, the health impacts of U.S. 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 of MATS are much larger than previously estimated, the actual costs appear to be substantially lower than projected by the EPA, and the total monetized benefits across all pollutants far outweigh the costs 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, 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. Global and regional trends in mercury emissions and concentrations, 2010-2015. Atmospheric Environment. Accepted.
 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.
 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.