Mercury

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From Mercury Science Fact Sheet, a work by the Science and Public Policy Institute

Contents

What is Mercury?

Mercury (Hg) is an element that has existed (and will continue to exist) naturally since the earth was formed 4.5 billion years ago. The oceans alone contain millions of tons of mercury.(1) There are two major forms of mercury emitted during fossil fuel combustion:

1. Oxidized, which is water soluble and can be washed out of the air into rivers, lakes, and streams.

2. Elemental, which is not water soluble and moves around in a global mercury cycle.

A small fraction (about one one-thousandth) of the oxidized mercury that ends up in waterways may be changed into an organic form called methylmercury (MeHg) which is the kind of mercury with which EPA is concerned. This type of mercury can be eaten by tiny organisms that are then eaten by small fish, resulting in possible bioaccumulation in larger fish eaten by humans.

Methylmercury is not emitted directly from fossil-fuel-fired power plants. It is produced and accumulated within the biosphere by a myriad of mercury transformation processes that do not depend upon the amount of inorganic mercury emitted from man-made sources.(2) The natural cyclical production and destruction is controlled by environmental factors and ecosystem processes that are largely beyond human control or intervention.

Where does Hg come from? – A Mostly Natural, World-wide Phenomena

The largest source of annual air-borne Hg is from natural sources such as volcanoes, forest fires, and oceans.(3) Emissions from Yellowstone National Park, for example, likely exceed that of all Wyoming coalfired power plants combined.(4) Under current estimates of total annual air-borne sources of Hg into the world cycle, US power plant emissions account for as little as 0.5%.(5)

A new estimate by scientists from the National Center for Atmospheric Research recently shown that mercury emissions from fires, mainly biomass burning from forests, from the lower 48 U.S. states and Alaska amount to about 44 tons per year.(6) This is of similar magnitude in comparison to the total mercury emissions from U.S. power plants. For another perspective, the 2008 UNEP mercury report gives 26 tons per year as the contribution from the cremation of human remains.(7)

The natural mercury emission from Earth’s crust is an important factor controlling mercury distribution in marine waters and the atmosphere, along with anthropogenic emissions. Main sources of mercury to seas are submarine volcanoes, mud volcanoes and cold gas vents. All current global estimates refer to atmospheric emissions only. Geological processes supplying Hg to soil, oceans, and inland water bodies also need to be quantified and considered in the global mercury budget and its natural cycling. When estimates of all natural sources are considered, including geothermal events under oceans and lakes, US power plants may account for as little as 0.002% of the entire annual world mercury emissions budget.(8)

Are Mercury levels changing?

From 1990 – 2000, total US anthropogenic Hg emissions decreased by 69 tons (to current level of about 107 tons), while Asia increased by over 500 tons (to current level of about 1204 tons) and Africa increased by about 230 tons (to about 407 tons). Table 5 of Pacyna et al. (2006)(9) reported the top seven mercury emitters in 2000 to be China, South Africa, India, Japan, Australia, U.S.A. and Russia with 604.7, 256.7, 149.9, 143.5, 123.5, 109.2 and 72.6 tons respectively. Again, a fact confirming the relatively small amount of mercury emissions from the U.S. sources, with US emission in 2000 ranked only 6th below even South Africa, India, Japan and Australia. With the most recent mercury emission budget available up to 2005, SPPI notes from the November 10, 2009 press release by the EPA(10) that from “1990 through 2005, [U.S.] emissions of mercury into the air decreased by 58 percent.” Further good news is that the latest projection of mercury emission in 2020 by Pacyna et al. (2010)(11) also suggest very small contribution, if not negligible role, from US industrial emissions.

In the Atlantic Ocean, comparisons of deep-sea fish (i.e., blue hake at depths of 1,000-3,000 m) found no change in tissue mercury concentration from 1880s to 1970s. The authors concluded: “The result supports the idea that the relatively high concentrations of mercury found in marine fish that inhabit the surface and deep waters of the open ocean result from natural processes, not 20th century industrial pollution.”(12)

In the Pacific Ocean, Princeton researchers found no increase in fish tissue mercury levels after comparing tuna samples from 1971 and 1998 (there was actually a minor decline). They expected to find a 9-26% increase. Those authors concluded the likely source of the mercury was deep ocean waters and sediments around geothermal vents: “Our findings that the concentration of mercury in tuna...has not changed over a period of time, during which anthropogenic mercury inputs...have increased, supports the idea that the source of methylmercury in tuna is not in surface waters. [This] provides prima facie evidence that this concentration is not responding to anthropogenic emissions irrespective of the mechanisms by which mercury is methylated in the oceans and accumulated in tuna.”(13)

As for human exposure to mercury (Hg and MeHg) through fish consumption, there is evidence of micro-traces of mercury (equal to and greater than modern levels) present in humans as long ago as 400AD. For example, eight 550-year old mummies from Alaska had mercury levels twice as high as pregnant women in Alaska today.(14)

What is the safe level (reference dose) of MeHg consumption according to EPA?

A reference dose (RfD) is the amount of a substance that can be consumed each day for a lifetime (70 years) without harm. The EPA mercury RfD is based on inappropriate studies of people who consume whale meat and blubber (a unique diet no one in the US has) containing multiple chemicals (PCBs, cadmium, pesticides, persistent organic pollutants, DDT, etc.) of which mercury is only one. The owners of the raw data refused to release it for scientific review. EPA downplayed studies that found no harm.

-EPA’s RfD is the most restrictive in the world – 10 times lower than the lowest level of concern.

-EPA is scaring people, especially pregnant women, from eating fish and benefiting from vital nutrition.(15)

What health benefits are lost from NOT eating fish due to concerns about mercury?

The Seychelles Island Study (Myers et al.) in the Indian Ocean, found benefits to children from mothers eating large quantities of fish (12-14 meals per week). These benefits included better eyesight and less hyperactivity in children.(16)

The Bristol England study found that high fish intake by pregnant women and young children was associated with higher child mental development scores, better eyesight and “no adverse developmental effects associated with mercury.”(17)

A Norwegian Study (Helland et al.) found that the nutrients in fish oil ingested during pregnancy and lactation “improves the intelligence of children at 4 years of age.”(18)

High fish or omega-3 fatty acids consumption may reduce risk for these conditions:

-Cardiovascular disease, coronary heart disease (CHD), and sudden deaths

-Breast cancer

-Prostate cancer

-Endometrial (inner lining of uterus) cancer

-Alzheimer disease

-Type 2 diabetes in women, and CHD in type 2 diabetic women

-Pre-term delivery and low birth weights, physiological and mental development of infants, and Postpartum depression19 and suicidal ideation.

References

1 E.g., Carmago (1993) Nature, vol. 365, 302.

2 Making Sense of State Fish Advisories, March 2005. http://scienceandpublicpolicy.org/mercury/sense_of_fish_advisories.html

3 Pacyna et al. (2003) Atmos Environ, vol. 37, S109-S117; Friedli et al., (2003) Atmos Environ, vol. 37, 253-267.

4 http://newsdesk.inel.gov/press_releases/2003/10-21mercury_testing.htm.

5 See Pyle and Mather (2003) Atmos Environ, vol. 37, 5115-5124 [also see: http://ff.org/centers/csspp/docs/20050103EPANODAComments.doc].

6 Wiedinmyer and Friedli (2007) Environmental Science & Technology, vol. 41, 8092-8098.

7 p. 18 of the 2008’s UNEP Mercury Report. UNEP’s “The Global Atmospheric Mercury Assessment: Sources, Emissions and Transport” (2008; updated and corrected May 2009). Available from: http://www.chem.unep.ch/Mercury/Atmospheric_Emissions/UNEP%20SUMMARY%20REPORT%20%20CORRECTED%20May09%20%20final%20for%20WEB%202008.pdf.

8 Rasmussen (1994) Environ Sci & Tech., vol. 28, 2233-2241.

9 Pacyna et al. (2006) Atmospheric Environment, vol. 40, 4048-4063.

10 EPA’s press release on this new report on November 10, 2009; available at: http://yosemite.epa.gov/OPA/ADMPRESS.NSF/ d0cf6618525a9efb85257359003fb69d/62b53c67bc92ef878525766a004b3456!OpenDocument.

11 Pacyna et al. 2010, Atmospheric Environment, vol. 44, 2487-2499.

12 Barber et al. (1984) Enviro Sci & Tech, vol.18, 552-555.

13 Kraepiel et al. (2004) Environ Sci & Tech, vol. 38, 4048 and see also Kraepiel et al., (2003), Environ Sci & Tech, vol. 37, 5551- 5558.

14 See Middaugh on pp 53-68 of July 24, 2002’s FDA’s Food Advisory Committee on MeHg. (http://www.fda.gov/OHRMS/DOCKETS/ac/02/transcripts/3872t2.htm) and also Arnold and Middaugh (2004) in Use of Traditional Foods in a Healthy Diet in Alaska: Risks in Perspective (available at: http://www.epi.hss.state.ak.us/bulletins/catlist.jsp?cattype=Mercury).

15 Oken et al. (2003), Obstetrics & Gynecology, vol. 102, 346-351.

16 Myers et al. (2003), Lancet, vol. 361, 1686-1692.

17 Daniels et al. (2004), Epidemiology, vol. 15, 394-402.

18 Helland et al. (2003), Pediatrics, vol. 111, e39-e44.

19 Hibbeln (2002) Journal of Affective Disorders, vol. 69, 16-29.

External Links

The Science and Public Policy Institute

The Heartland Institute

Willie Soon EPA NESHAP Proposed Rule Notice and Comment

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