Mercury in fish

Fish and shellfish concentrate mercury in their bodies, often in the form of methylmercury, a highly toxic organomercury compound. Fish products have been shown to contain varying amounts of heavy metals, particularly mercury and fat-soluble pollutants from water pollution. Species of fish that are long-lived and high on the food chain, such as marlin, tuna, shark, swordfish, king mackerel and tilefish (Gulf of Mexico) contain higher concentrations of mercury than others.[1]

Nearby anthropogenic sources, such as coal burning and mining of iron, can contaminate water sources with methylmercury, which is efficiently absorbed in the bodies of fish. Through the process of biomagnification, mercury levels in each successive predatory stage increase.

Mercury is known to bioaccumulate in humans, so bioaccumulation in seafood carries over into human populations, where it can result in mercury poisoning. Mercury is dangerous to both natural ecosystems and humans because it is a metal known to be highly toxic, especially due to its ability to damage the central nervous system.[2] In human-controlled ecosystems of fish, usually done for market production of wanted seafood species, mercury clearly rises through the food chain via fish consuming small plankton, as well as through non-food sources such as underwater sediment.[3]

The presence of mercury in fish can be a particular health concern for women who are or may become pregnant, nursing mothers, and young children.

Biomagnification

The consumption of fish is by far the most significant source of ingestion-related mercury exposure in humans and animals.[4] Mercury and methyl mercury are present in only very small concentrations in seawater. However, they are absorbed, usually as methyl mercury, by algae at the start of the food chain. This algae is then eaten by fish and other organisms higher in the food chain. Fish efficiently absorb methyl mercury, but excrete it very slowly.[5] Methyl mercury is not soluble and therefore not excreted. Instead, it accumulates, primarily in the viscera, although also in the muscle tissue.[6] This results in the bioaccumulation of mercury, in a buildup in the adipose tissue of successive trophic levels: zooplankton, small nekton, larger fish, and so on.[7] The older that such fish become, the more mercury they may have absorbed. Anything that eats these fish within the food chain also consumes the higher level of mercury that the fish have accumulated, including humans.[7] This process explains why predatory fish such as swordfish and sharks or birds like osprey and eagles have higher concentrations of mercury in their tissue than could be accounted for by direct exposure alone. Species on the food chain can amass body concentrations of mercury up to ten times higher than the species they consume. This process is called biomagnification. For example, herring contains mercury levels at about 0.1 parts per million, while shark contains mercury levels greater than 1 part per million.[8]

Origins of mercury pollution

Terrestrial mercury pollution

There are three types of mercury emission: anthropogenic, re-emission, and natural, including volcanoes and geothermal vents. Anthropogenic sources are responsible for 30% of all emissions, while natural sources are responsible for 10%, and re-emission accounts for the other 60%. While re-emission accounts for the largest proportion of emissions, it is likely that the mercury emitted from these sources originally came from anthropogenic sources.[9]

Anthropogenic sources include coal burning, cement production, oil refining, artisan and small-scale gold mining, wastes from consumer products, dental amalgam, the chlor-alkali industry, production of vinyl chloride, and the mining, smelting, and production of iron and other metals.[9] The total amount of mercury released by mankind in 2010 was estimated to be 1,960 metric tons. The majority of this comes from coal burning and gold mining, accounting for 24% and 37% of total anthropogenic output respectively.[9]

Re-emission, the largest emitter, occurs in a variety of ways. It is possible for mercury that has been deposited in soil to be re-emitted into the mercury cycle via floods. A second example of re-emission is a forest fire; mercury that has been absorbed into plant life is re-released into the atmosphere. While it is difficult to estimate the exact extent of mercury re-emission, it is an important field of study. Knowing how easily and how often previously emitted mercury can be released helps us learn how long it will take for a reduction in anthropogenic sources to be reflected in the environment. Mercury that has been released can find its way into the oceans. A 2008 model estimated the total amount of deposition into the oceans that year to be 3,700 metric tons. It is estimated that rivers carry as much as 2,420 metric tons.[9] Much of the mercury deposited in the oceans is re-emitted, however; as much as 300 metric tons is converted into methyl mercury. While only 13% of this finds its way into the food chain, that is still 40 metric tons a year.[9]

Much (an estimated 40%) of the mercury that eventually finds its way into fish originates with coal-burning power plants and chlorine production plants.[10] The largest source of mercury contamination in the United States is coal-fueled power plant emissions.[11] Chlorine chemical plants use mercury to extract chlorine from salt, which in many parts of the world is discharged as mercury compounds in waste water, though this process has been largely replaced by the more economically viable membrane cell process, which does not use mercury. Coal contains mercury as a natural contaminant. When it is fired for electricity generation, the mercury is released as smoke into the atmosphere. Most of this mercury pollution can be eliminated if pollution-control devices are installed.[10]

Mercury in the United States frequently comes from power plants, which release about 50% of the nation's mercury emissions.[12] In other countries, such as Ghana, gold mining requires mercury compounds, leading to workers receiving significant quantities of mercury while performing their jobs. Such mercury from gold mines is specifically known to contribute to biomagnification in aquatic food chains.[13]

Elemental mercury often comes from coal power plants, and oxidized mercury often comes from incinerators. Oil-fired power plants also contribute mercury to the environment.[2] The energy industry therefore is a key player in the introduction of mercury into the environment. When addressing the issue of reducing seafood mercury bioaccumulation on a global scale, it is important to pinpoint major energy producers and consumers whose exchange of energy may be the root of the problem.

Aquatic mercury pollution

The farming of aquatic organisms, known as aquaculture, often involves fish feed that contains mercury. A study by Jardine has found no reliable connection between mercury in fish food affecting aquaculture organisms or aquatic organisms in the wild.[14] Even so, mercury from other sources may affect organisms grown through aquaculture. In China, farmed fish species, such as bighead carp, mud carp, and Siniperca chuatsi, carried 90% of total mercury content in all of the measured fish in a study by Cheng. This study also concluded that mercury bioaccumulates through food chains even in controlled aquaculture environments. Both total mercury and methyl mercury absorption was found to be derived from sediments containing mercury, not mainly from fish feed.[3]

The Hawaii Institute of Marine Biology has noted that fish feed used in aquaculture often contains heavy metals such as mercury, lead, and arsenic, and has dispatched these concerns to organizations such as the Food and Agriculture Organization of the United Nations.

Mercury can get into freshwater systems by point sources and extended flooding.[7] In Canada, mercury poisoning in Grassy Narrows was likely caused by a spill at a paper mill, which is a point source. Non-point sources include floods that create hospitable habitats for bacteria that can convert mercury to methylmercury, which is the toxic form that bioaccumulates through aquatic food webs. The effects of these different sources of mercury have been studied at the Experimental Lakes Area in Ontario, Canada, using research procedures including whole-lake ecosystem experiments and non-lethal fish muscle biopsies.[7]

Controlling output of mercury pollution sources

A study that was led by scientists from Harvard University and U.S. Geological Survey has determined that in the next several decades there will be a 50 percent increase in mercury levels. The study also shows that the increases are connected through industrial emissions and are not natural as previously thought.However, by decreasing emissions from industrial plants, the possibility of decreasing the high level of mercury remains plausible.[15] Several nations are currently implementing systems that will detect and therefore later be able to control the output of mercury into the atmosphere. Air pollution control devices (APCDs) have been implemented in South Korea as the government is starting to take inventory of mercury sources. Mercury pollution can also be removed by electrostatic precipitators (ESPs). Bag-based filters are also used in factories that may contribute mercury to the environment. Flue-gas desulfurization, normally used to eliminate sulfur dioxide, can also be used in conjunction with APCDs to remove additional mercury before exhausts are released into the environment.[2] Even so, countries such as South Korea have only begun to use inventories of mercury sources, calling into question how fast anti-mercury measures will be put into factories.

Health effects and outcomes

Disparate impacts

Mercury content in fish does not affect all populations equally. Certain ethnic groups, as well as young children, are more likely to suffer the effects of methyl mercury poisoning. In the United States, Wallace gathered data that indicated 16.9% of women who self-identify as Native American, Asian, Pacific Islander, or multiracial exceed the recommended reference dose of mercury.[16] A study done on children of the Faroe Islands in the North Atlantic showed neurological problems stemming from mothers consuming pilot whale meat during pregnancy[17] (see Whaling in the Faroe Islands). A 2020 NBER paper found that in coastal Colombia, those born during periods when fish catches have high mercury content have worse educational and labor market outcomes than those born during periods of low mercury content in fish.[18]

Regulation and health

While various studies have shown high concentrations of mercury accumulated in fish, medical cases often go unreported and pose a difficulty in correlating mercury in fish with human poisoning. Environmental issues cover a broad range of areas, but medical cases that are associated with pollutants released into the environment by factories or construction areas cause public health issues that affect not only the environment but also human well-being. Substances poisonous to the human body in a particular amount or dose may not cause any symptoms over time. While there are limits to how much of anything the body can have, mercury is a particular poison that produces immediate physical symptoms when the body has been accumulating it over a period of time.

In the United States, the Environmental Protection Agency measures the amount of mercury concentrated in human blood that does not pose fatal health outcomes. The agency is in charge of enforcing regulations and policies that cover a range of environmental topics.[19] Analysis of blood mercury concentrations in childbearing women has proved that exposure to methyl mercury (MeHg) occurs primarily through the consumption of fish.[20] The U.S. FDA highly recommends against pregnant woman and young children consuming raw fish. Pregnant women and young children often lack strong immune systems and are more at risk for foodborne illnesses.[21]

Medical cases and exposure to mercury

In the United States, the EPA serves as an advisory organ to set the levels of mercury that are non-fatal in humans. Symptoms of exposure to high levels of methyl mercury include disturbed vision, hearing, and speech, lack of coordination, and muscle weakness. Medical studies have examined the correlation of fish consumption and health issues. American studies have presented evidence of fish consumption and its effects on child development. Longitudinal studies agree that human activities are what release and accumulate mercury in marine life.[22] Addressing the issues of fish consumption forces health officials to recognize the sources of mercury in the human body. Specific Native American tribes are vulnerable to a high exposure of mercury. Studies have determined that these native peoples in the United States suffer more from mercury poisoning and illness than any other cohort group in the country. This is due to the fact that fish is a main source of protein. Exposure risk was assessed through a medical study, thus raising judicial issues of whether the public health of these groups is a priority in the United States.[23]

Work and exposure

Most cases that arise are due to work exposure or medicinal poisoning. Environmental justice advocates can relate these mercury cases to the unregulated amount of mercury that enters the environment. Workers can be exposed to mercury through the manufacture of fluorescent tubes, chloralkali, or acetaldehyde among other products. Anthropogenic sources and places where mercury is released or used as a solid or vapor puts these has caused fatigue, dizziness, hyperhidrosis, chest congestion, and loss of motor skills. When taken to the hospital, the neurotoxicity levels had already exceeded the maximum amounts.[24] Over-the-counter medicines have been shown to have traces of mercurous chloride. Medical research reported that the children who received doses of these medicines experienced physical symptoms such as "drooling, irregular arm movements, and impaired gait".[25] Exposures to this result in severe physical impairments unregulated chemicals that are put in products. The intake of laxatives that contained about 120 mg of mercurous chloride has also been cases of mercury's toxicity.[26]

Even in countries, such as Sweden, that have phased out mercury in the dental industry and manufacturing, lingering quantities of mercury still exist in lakes and coastal areas. Moreover, global contributions of mercury to the environment also affect that country. A study in Sweden selected 127 women who had a high level of fish consumption. Around 20% of the women selected, after hair and blood samples, were found to have exceeded the EPA's recommended reference dose of 0.1 micrograms of methyl mercury per kilogram of body weight. Additionally, the study concluded that there was "no margin of safety for neuraldevelopmental effects in fetus[es]"[27] without removing the offending species of fish from the diets of the women. This indicates that families intending to raise children should be especially careful about exposing their unborn babies to toxic mercury via fish.

Children exposed to mercury are particularly susceptible to poisoning since the ratio of food, water, and air intake versus individual body weight is much higher than that of adults.[28] Additionally, children undergo fast growth which causes them to be more susceptible to damaging exposure to methylmercury, as well as the long term consequences of such exposure during childhood development.[28] Young age plays an important role in terms of damage caused by mercury, and much literature on mercury focuses on pregnant women and specific precautions designed to prevent youth mercury exposure. Prenatal methylmercury exposure does cause behavioral problems in infants and worsened cognitive test performance. Additionally, Hughner estimates that 250,000 women may be exposing their unborn babies to levels of methyl mercury above recommended federal levels.[29]

Economically, there does not seem to be a difference in mercury exposure based on socioeconomic bracket and the ability to buy fish from the market. One study shows "no significant differences in mercury levels in tuna, bluefish, and flounder as a function of type of store or economic neighborhood".[30]

By nation

Certain countries have cultural differences that lead to more fish consumption and therefore more possible exposure to seafood methylmercury. In Ghana, the local population traditionally consumes large quantities of fish, leading to potentially dangerous amounts of mercury in the bloodstream.[13] In the Amazonian Basin, during the rainy season, herbivorous fish dominate the diet of 72.2% of the women selected from a particular Amazonian village. Analysis also shows increase of mercury content in the hair of humans who eat fish on a daily basis in the Amazon.[31]

The most serious case of mercury poisoning in recent history was in the Japanese city of Minamata, in the 1950s. Minamata poisoning proves that significant prenatal and postnatal exposure to high levels of methylmercury causes serious neurological problems. Minamata victims also show higher than normal signs of psychiatric diseases, along with those diseases being caused by underlying neurological issues.[32]

A 2014 USGS survey of mercury levels in the United States water system found that methylmercury concentrations in fish were typically highest in wetland areas including the coastal plain streams in the Southeast. Fish methylmercury levels were also high in the Western US, but only in streams that had been mined for mercury or gold.[33]

Minamata disease

In the 1950s, inhabitants of the seaside town of Minamata, on Kyushu island in Japan, noticed strange behavior in animals. Cats would exhibit nervous tremors, and dance and scream. Within a few years this was observed in other animals; birds would drop out of the sky. Symptoms were also observed in fish, an important component of the diet, especially for the poor. When human symptoms started to be noticed around 1956 an investigation began. Fishing was officially banned in 1957. It was found that the Chisso Corporation, a petrochemical company and maker of plastics such as vinyl chloride, had been discharging heavy metal waste into the sea for decades. They used mercury compounds as catalysts in their syntheses. It is believed that about 5,000 people were killed and perhaps 50,000 have been to some extent poisoned by mercury. Mercury poisoning in Minamata, Japan, is now known as Minamata disease.

Seafood consumption benefits

The American College of Obstetricians and Gynecologists note that, considering all the dangers and benefits, the overall result of eating fish in the United States is likely to improve personal health rather than damage it.[17] The college argues that the omega-3 polyunsaturated fatty acids found in fish have a health benefit that outweighs the harm from mercury or polychlorinated biphenyls. Even so, the College also suggests limiting fish consumption for pregnant women. A risk-benefit study weighing the risks of mercury consumption against the benefits derived from fish in Alaska showed that the benefits outweigh the risks when consuming salmon for both cardiovascular health and infant neurological development, and that MeHg data for non-oily fish needs to be of high quality before relative risk can be reliably identified. [34] The Seychelles Child Development Study traced more than seven hundred mother-child pairs for nine years, and found no neurological problems in the children resulting from both prenatal and postnatal methylmercury exposure. A study done with marketed fish in Oman concluded that, except in a few rare cases, the fish available for consumption had lower levels of mercury than limits defined by various health organizations.[35] Clearly, these studies call into question whether or not normal everyday consumption of fish is dangerous in any way, and at very least justify the creation of place-based and culturally relevant consumption advisories.[36] They do not take into account cases of severe mercury poisoning, such as that found in Minamata disease.

Selenium is an element that is known to counteract some of the dangers of ingesting mercury.[29] Multiple studies have been done, such as those in New Jersey and Sweden, that take into account selenium as well as mercury levels. Fish often do contain selenium in conjunction with bioaccumulated mercury, which may offset some of the dangers associated with the mercury ingested.

Levels of contamination

Most-contaminated fish species

The danger level from consuming fish depends on species and size. Size is the best predictor of increased levels of accumulated mercury. Sharks, such as the mako shark, have very high levels of mercury. A study on New Jersey coastal fish indicated that one third of the sampled fish had levels of mercury above 0.5 parts per million, a level that could pose a human health concern for consumers who regularly eat this fish.[29] Another study of marketplace fish caught in waters surrounding Southern Italy showed that, undoubtedly, greater fish weight leads to additional mercury found in fish body tissues. Moreover, the concentration, measured in milligrams of mercury per kilogram of fish, steadily increases with the size of the fish. Anglerfish off the coast of Italy were found with concentrations as high as 2.2 milligrams of mercury per kilogram, higher than the recommended limit of 1 milligram of mercury per kilogram. Annually, Italy catches approximately a third of its fish from the Adriatic Sea, where these anglerfish were found.[37]

Fish that consume their prey in a certain manner may contain much higher concentrations of mercury than other species. Grass carp off the coast of China hold far less internal mercury than do bighead carp. The reason for this is that bighead carp are filter feeders, while grass carp are not. Thus, bighead carp gather more mercury by eating large amounts of small plankton, as well as sucking up sediments that collect a sizable amount of methyl mercury.[3]

Mercury levels in commercial fish and shellfish
species Mean
(ppm)[1]
Std dev
(ppm)[1]
Median
(ppm)[1]
Comment Trophic
level[38]
Max age
(years)[38]
Tilefish (Gulf of Mexico) 1.123 n/a n/a Mid-Atlantic tilefish has lower mercury levels
and is considered safe to eat in moderation.[1]
3.6 35
Swordfish 0.995 0.539 0.870 4.5 15
Shark 0.979 0.626 0.811
Mackerel (king) 0.730 n/a n/a 4.5 14
Tuna (bigeye) 0.689 0.341 0.560 Fresh/frozen 4.5 11
Orange roughy 0.571 0.183 0.562 4.3 149
Marlin* 0.485 0.237 0.390 4.5
Mackerel (Spanish) 0.454 n/a n/a Gulf of Mexico 4.5 5
Grouper 0.448 0.278 0.399 All species 4.2
Tuna 0.391 0.266 0.340 All species, fresh/frozen
Bluefish 0.368 0.221 0.305 4.5 9
Sablefish 0.361 0.241 0.265 3.8 94
Tuna (albacore) 0.358 0.138 0.360 Fresh/frozen 4.3 9
Patagonian toothfish 0.354 0.299 0.303 AKA Chilean sea bass 4.0 50+[39]
Tuna (yellowfin) 0.354 0.231 0.311 Fresh/frozen 4.3 9
Tuna (albacore) 0.350 0.128 0.338 Canned 4.3 9
Croaker white 0.287 0.069 0.280 Pacific 3.4
Halibut 0.241 0.225 0.188 4.3
Weakfish 0.235 0.216 0.157 Sea trout 3.8 17[40]
Scorpionfish 0.233 0.139 0.181
Mackerel (Spanish) 0.182 n/a n/a South Atlantic 4.5
Monkfish 0.181 0.075 0.139 4.5 25
Snapper 0.166 0.244 0.113
Bass 0.152 0.201 0.084 Striped, black, and black sea 3.9
Perch 0.150 0.112 0.146 Freshwater 4.0
Tilefish (Atlantic) 0.144 0.122 0.099 3.6 35
Tuna (skipjack) 0.144 0.119 0.150 Fresh/frozen 3.8 12
Buffalofish 0.137 0.094 0.120
Skate 0.137 n/a n/a
Tuna 0.128 0.135 0.078 All species, canned, light
Perch (ocean) * 0.121 0.125 0.102
Cod 0.111 0.152 0.066 3.9 22
Carp 0.110 0.099 0.134
Lobster (American) 0.107 0.076 0.086
Sheephead (California) 0.093 0.059 0.088
Lobster (spiny) 0.093 0.097 0.062
Whitefish 0.089 0.084 0.067
Mackerel (chub) 0.088 n/a n/a Pacific 3.1
Herring 0.084 0.128 0.048 3.2 21
Jacksmelt 0.081 0.103 0.050 3.1
Hake 0.079 0.064 0.067 4.0
Trout 0.071 0.141 0.025 Freshwater
Crab 0.065 0.096 0.050 Blue, king and snow crab
Butterfish 0.058 n/a n/a 3.5
Flatfish * 0.056 0.045 0.050 Flounder, plaice and sole
Haddock 0.055 0.033 0.049 Atlantic
Whiting 0.051 0.030 0.052
Mackerel (Atlantic) 0.050 n/a n/a
Croaker (Atlantic) 0.065 0.050 0.061
Mullet 0.050 0.078 0.014
Shad (American) 0.039 0.045 0.045
Crayfish 0.035 0.033 0.012
Pollock 0.031 0.089 0.003
Catfish 0.025 0.057 0.005 3.9 24
Squid 0.023 0.022 0.016
Salmon * 0.022 0.034 0.015 Fresh/frozen
Anchovies 0.017 0.015 0.014 3.1
Salmon * 0.014 0.021 0.010 Canned
Sardine 0.013 0.015 0.010 2.7
Tilapia * 0.013 0.023 0.004
Oyster 0.012 0.035 n/d
Clam * 0.009 0.011 0.002
Shrimp * 0.009 0.013 0.001 6.5[41]
Scallop 0.003 0.007 n/d
* indicates only methylmercury was analyzed (all other results are for total mercury)
n/a – data not available
n/d – below detection level (0.01ppm)

US government scientists tested fish in 291 streams around the country for mercury contamination. They found mercury in every fish tested, according to the study by the U.S. Department of the Interior. They found mercury even in fish of isolated rural waterways. Twenty-five percent of the fish tested had mercury levels above the safety levels determined by the U.S. Environmental Protection Agency for people who eat the fish regularly.[11]

Legislation

Japan

Since the Minamata disaster, Japan has improved on its mercury regulation. During the 1970s Japan made strides to reduce mercury demand and production. Chief among these efforts was the reduction of inorganic mercury produced by mines. It was halted by 1974, and demand fell from 2,500 tons per year in 1964, its peak, to 10 tons per year in recent years.[42] Since these initial strides, Japan has introduced a list of regulations governing the mercury content of a variety of materials.

Japan Mercury Regulation[42]
CategoryRegulationResult
CosmeticsPharmaceutical Affairs ActBan the use of mercury and its compounds
AgricultureAgricultural Chemicals Control ActBan the use of mercury and its compounds as an active ingredient
Household CommoditiesAct on Control of Household Products Containing Hazardous SubstancesNo mercury in household adhesives, household paints, household wax, shoe polish, shoe cream, diapers, bibs, undergarments, gloves, and socks
Pharmaceutical ProductsPharmaceutical Affairs ActNo use of mercury compounds in oral preparations. No use of mercury compounds, other than mercurochrome, as an active ingredient. Mercury as a preservative only if no other option is available.
AirAir Pollution Control LawNo more than 40 ng/m3
WaterBasic Environment Law and Water Pollution Control ActEnvironmental quality standard: no more than 0.0005 mg/L in waterway and ground water. Effluent standard: no more than 0.005 mg/L in effluence.
SoilBasic Environment Law and Soil Contamination Countermeasures ActEnvironmental quality standard: no more than 0.0005 mg/L sample solution. Elution standard: no more than 0.0005 mg/L. Content standard: no more than 15 mg/kg

Regulation of these potential sources of pollution reduces the amount of mercury that ends up in fish and, through biomagnification, in humans. In addition to enacting legislation controlling the mercury levels in potential pollutants, Japan has directly influenced the environment by issuing regulations setting acceptable levels of environmental mercury pollution.

It is Japan's goal to promote international mercury legislation in hopes of preventing any country from experiencing what it did.[42] Despite Japan's extensive regulation and experience with mercury-based disasters, there is still little information provided to the public. The Japanese Federal Fish Advisory's recommendations are less strict than those in America.[43]

United States

Fish advisory chart issued by U.S. Environmental Protection Agency and Food and Drug Administration

The United States has regulated mercury emissions under the authority of the Clean Air Act.

The Environmental Protection Agency (EPA) first attempted to regulate power plant mercury emissions with the Clean Air Mercury Rule in 2005.[44] The George W. Bush administration intended for the regulation to use a cap-and-trade system to control emissions across multiple industries. The rule was challenged in litigation, and in 2008 the U.S. Court of Appeals for the District of Columbia Circuit vacated the rule, stating that EPA had improperly excluded power plants from designation as emitting hazardous air pollutants.[45]

EPA subsequently classified mercury emissions from power plants as hazardous under section 112 of the Clean Air Act. The 2012 Mercury and Air Toxics Standards (MATS) regulation, issued by the Barack Obama administration, targets airborne mercury emissions from power plants and other stationary sources.[46][47] Airborne mercury is dissolved in the oceans, where microorganisms convert waterborne mercury into methyl mercury, which enters the food chain and is stored in fish tissue.

EPA stated that the MATS regulation would prevent about 90% of power plant mercury.[47] The agency estimated the total expected health benefits are estimated at $37 billion–$90 billion by 2016. EPA estimated the economic cost at $9.6 billion annually..

In 2020 the Trump administration attempted to weaken the MATS rule by disavowing EPA's previous calculations and justifications, thereby making the rule subject to legal challenges.[48]

European Union

In EU, the regulation (EU) 2017/852[49] covers the full life cycle of mercury. This legislation prohibits the manufacture, export and import of a large range of mercury-added products; puts an end to all uses of mercury catalysts and large electrodes in industrial processes and reduces the use of and pollution from dental amalgamRecently, the EU estimated the Mercury content in the topsoils based on a large Land Cover Survery named LUCAS.[50] The mercury content in EU topsoils has a median of 38 μg per Kg with a total content of around 45,000 tons[51] in the 0–20 cm of EU.

International

Legislation on a global scale is believed by some to be needed for this issue because mercury pollution is estimated to be so far-reaching. Pollution from one country does not stay localized to that country. Despite the need by some, international regulation has been slow to take off. The first forms of international legislation appeared in the 1970s, beginning as agreements about shared bodies of water.[52] The next step was the Stockholm Declaration, which urged countries to avoid polluting the oceans by dumping.[53] The 1972 Oslo Convention and the 1974 Paris Convention were adopted by parts of Europe. Both lessened polluting the ocean with mercury, the former by banning the dumping of ships and aircraft into the ocean and the latter by obligating participants to reduce land-based pollution on coastlines.[54][55] The first real global legislation regarding mercury pollution was the Basel Convention of 1989. This convention attempts to reduce the movement of mercury across borders and primarily regulates the import and export of toxic chemicals, including mercury.[52] In 1998 the Convention on Long-Range Transboundary Air Pollution was adopted by most of the European Union, the United States, and Canada. Its primary objective is to cut emissions of heavy metals. The convention is the largest international agreement on mercury established to date.[52] In the early 21st century, the focus of mercury regulation has been on voluntary programs.[52] The next phase in legislation is a global effort, and this appears to be what the Minamata Convention hopes to accomplish. The Minamata Convention, named after the Japanese city that suffered horribly from mercury pollution, has taken four years of negotiation but was finally adopted by delegates from over 140 countries. The convention will come into power after 50 countries have signed it. The Minamata Convention will require all participants to eliminate, where possible, the release of mercury from small-scale gold mining. It will also require a sharp reduction in emission from coal burning.[56]

Current advice

The complexities associated with mercury transport and environmental fate are described by USEPA in their 1997 Mercury Study Report to Congress.[57] Because methyl mercury and high levels of elemental mercury can be particularly toxic to a fetus or young children, organizations such as the U.S. EPA and FDA recommend that women who are pregnant or plan to become pregnant within the next one or two years, as well as young children, avoid eating more than 6 ounces (170g, one average meal) of fish per week.[58]

In the United States, the FDA has an action level for methylmercury in commercial marine and freshwater fish that is 1.0 parts per million (ppm). In Canada, the limit for the total of mercury content is 0.5 ppm. The Got Mercury? website includes a calculator for determining mercury levels in fish.[59]

Species with characteristically low levels of mercury include shrimp, tilapia, salmon, pollock, and catfish (FDA March 2004). The FDA characterizes shrimp, catfish, pollock, salmon, sardines, and canned light tuna as low-mercury seafood, although recent tests have indicated that up to 6 percent of canned light tuna may contain high levels.[60] A study published in 2008 found that mercury distribution in tuna meat is inversely related to the lipid content, suggesting that the lipid concentration within edible tuna tissues has a diluting effect on mercury content.[61] These findings suggest that choosing to consume a type of tuna that has a higher natural fat content may help reduce the amount of mercury intake, compared to consuming tuna with a low fat content. Also, many of the fish chosen for sushi contain high levels of mercury.[62]

According to the US Food and Drug Administration (FDA), the risk from mercury by eating fish and shellfish is not a health concern for most people.[63] However, certain seafood might contain levels of mercury that may cause harm to an unborn baby (and especially its brain development and nervous system). In a young child, high levels of mercury can interfere with the development of the nervous system. The FDA provides three recommendations for young children, pregnant women, and women of child-bearing age:

  1. Do not eat shark, swordfish, king mackerel, or tilefish (Gulf of Mexico) because they might contain high levels of mercury.
  2. Eat up to 12 ounces (2 average meals of 170 g each) a week of a variety of fish and shellfish that are lower in mercury. Five of the most commonly eaten fish and shellfish that are low in mercury are: shrimp, canned light tuna, salmon, pollock, and catfish. Another commonly eaten fish, albacore or ("white") tuna depending on its origin might have more mercury than canned light tuna. So, when choosing your two meals of fish and shellfish, it is recommended that you should not eat more than up to 6 ounces (one average meal) of albacore tuna per week.
  3. Check local advisories about the safety of fish caught by family and friends in your local lakes, rivers, and coastal areas. If no advice is available, eat up to 6 ounces (one average meal of 170 g) per week of fish you catch from local waters, but consume no other fish during that week.

Research suggests that selenium content in fish is protective against the toxic effects of methylmercury content.[64] Fish with higher ratios of selenium to methylmercury (Se:Hg) are better to eat since the selenium binds to the methylmercury allowing it to pass through the body un-absorbed.

In 2012 the European Food Safety Authority (EFSA) reported on chemical contaminants they found in the food of over 20 European countries. They established that fish meat and fish products were primarily responsible for methylmercury in the diet of all age classes. Particularly implicated were swordfish, tuna, cod, pike, whiting and hake. The EFSA recommend a tolerable weekly intake for methylmercury of 1.3 μg/kg body weight.[65]

See also

References

  1. The mercury levels in the table, unless otherwise indicated, are taken from: Mercury Levels in Commercial Fish and Shellfish (1990-2010) Archived 2015-05-03 at the Wayback Machine U.S. Food and Drug Administration. Accessed 8 January 2012.
  2. Park, K. S.; Seo, Y.-C.; Lee, S.J.; Lee, J.H. (2008). "Emission and Speciation of Mercury from various Combustion Sources". Powder Technology. 180 (1–2): 151–156. doi:10.1016/j.powtec.2007.03.006.
  3. Cheng, Zhang (2011). "Mercury Biomagnification in the Aquaculture Pond Ecosystem in the Pearl River Delta". Archives of Environmental Contamination and Toxicology. 61 (3): 491–499. doi:10.1007/s00244-010-9641-z. PMID 21290120. ProQuest 913807855.
  4. United States Environmental Protection Agency (December 1997). Mercury Study Report to Congress (PDF). 3. Washington, D.C.: United States Environmental Protection Agency. Archived (PDF) from the original on 2011-02-03.
  5. Croteau, M.; Luoma, S. N.; Stewart, A. R (2005). "Trophic transfer of metals along freshwater food webs: Evidence of cadmium biomagnification in nature". Limnol. Oceanogr. 50 (5): 1511–1519. doi:10.4319/lo.2005.50.5.1511.
  6. Cocoros, G.; Cahn, P. H.; Siler, W. (1973). "Mercury concentrations in fish, plankton and water from three Western Atlantic estuaries" (PDF). Journal of Fish Biology. 5 (6): 641–647. doi:10.1111/j.1095-8649.1973.tb04500.x. Archived from the original (PDF) on 2014-02-11.
  7. "Mercury: What it does to humans and what humans need to do about it". IISD Experimental Lakes Area. 2017-09-23. Retrieved 2020-07-13.
  8. EPA (U.S. Environmental Protection Agency). 1997. Mercury Study Report to Congress. Vol. IV: An Assessment of Exposure to Mercury in the United States . EPA-452/R-97-006. U.S. Environmental Protection Agency, Office of Air Quality Planning and Standards and Office of Research and Development.
  9. "Global Mercury Assessment 2013: Sources, Emissions, Releases and Environmental Transport" (PDF). UNEP Chemicals Branch, Geneva, Switzerland. 2013. Archived (PDF) from the original on 2014-04-01. Retrieved 18 Apr 2014.
  10. Mercury contamination in fish: Know where it's coming from Archived 2010-02-04 at the Wayback Machine Natural Resources Defense Council. Retrieved 23 January 2010
  11. New York Times, 2009 Aug. 19, "Mercury Found in Every Fish Tested, Scientists Say," Archived 2016-12-29 at the Wayback Machine
  12. "Mercury and Air Toxics Standard". US EPA. 21 Dec 2011. Archived from the original on 27 March 2014. Retrieved 7 April 2014.
  13. Adimado, A (2002). "Mercury in Human Blood, Urine, Hair, Nail, and Fish from the Ankobra and Tano River Basins in Southwestern Ghana". Bulletin of Environmental Contamination and Toxicology. 68 (3): 339–46. doi:10.1007/s001280259. PMID 11993807. ProQuest 18913728.
  14. Jardine, Laura (2007). "Mercury Cycling through Finfish Aquaculture within the Lower Bay of Fundy, Canada: Possibilities for Control in Support of the Health of Coastal Communities". ProQuest 759317881. Cite journal requires |journal= (help)
  15. "Big increase in ocean mercury found; study predicts more human threat from fish — Environmental Health News". www.environmentalhealthnews.org. Archived from the original on 2015-11-20. Retrieved 2015-11-23.
  16. Wallace, Sharon D. (7 Sep 2012). "Using Information Technology to Reduce a Health Risk: Effect of a Mercury Calculator on Consumer Fish Choices and Test of a Model for Technology Acceptance by Fish Consumers": 5. Archived from the original on 2014-05-07. Retrieved 8 Apr 2014. Cite journal requires |journal= (help)
  17. "Medical Letter: Mercury in Fish". American College of Obstetricians and Gynecologists. 115 (5): 1077–1078. May 2010. doi:10.1097/AOG.0b013e3181db2783.
  18. Rosenzweig, Mark R; Villagran, Rafael J. Santos (2020). "Is Fish Brain Food or Brain Poison? Sea Surface Temperature, Methyl-mercury and Child Cognitive Development". Cite journal requires |journal= (help)
  19. Jorgensen, Budtz; Grandjean, P; Weihe, P (2007). "amounts". Environmental Health Perspectives. 115 (3): 323–327. doi:10.1289/ehp.9738. PMC 1849938. PMID 17431478.
  20. Weiss, Davidson. "Children" (PDF).
  21. "Eating Fish: What Pregnant Women and Parents Should Know". www.fda.gov. FDA. Archived from the original on 1 August 2017. Retrieved 1 May 2018.
  22. Oken, Emily; Bellinger, D. C. (2008). "Fish Consumption Effects". Current Opinion in Pediatrics. 20 (2): 178–183. doi:10.1097/MOP.0b013e3282f5614c. PMC 2581505. PMID 18332715.
  23. O'neill, Catherine. "Natives". Archived from the original on 2016-03-04.
  24. Mahaffey, KR (2005). "Where We Stand on Mercury Pollution and its Health Effects on Regional and Global Scales". exposure. Springer. pp. 1–21. doi:10.1007/0-387-24494-8_1. ISBN 978-0-387-24493-8. ISBN 9780387244938, 9780387244945.
  25. Peckham; Choi, B. H. (1988). "Abnormal neuronal distribution within the cerebral cortex". Acta Neuropathologica. 76 (3): 222–6. doi:10.1007/bf00687768. PMID 3213424.
  26. Weiss; Trip, L; Mahaffey, K. R. (1999). "Human exposures to inorganic mercury". Public Health Reports. 114 (5): 400–401. PMC 1308511. PMID 10590760.
  27. Bjornberg, K. A.; Vahter, Marie; Grawé, Kierstin Petersson; Berglund, Marika (2005). "Methyl Mercury Exposure in Swedish Women with High Fish Consumption". Science of the Total Environment. 341 (1–3): 45–52. doi:10.1016/j.scitotenv.2004.09.033. PMID 15833240.
  28. Landrigan, Philip; Rauh, Virginia A.; Galvez, Maida P. (2010). "Environmental Justice and the Health of Children". Mount Sinai Journal of Medicine. 77 (2): 178–187. doi:10.1002/msj.20173. PMC 6042867. PMID 20309928.
  29. Burger, Joanna; Gochfeld, Michael (2011). "Mercury and Selenium Levels in 19 Species of Saltwater Fish from New Jersey as a Function of Species, Size, and Season". Science of the Total Environment. 409 (8): 1418–1429. doi:10.1016/j.scitotenv.2010.12.034. PMC 4300121. PMID 21292311.
  30. Burger, Joanna (Mar 2005). "Mercury in Commercial Fish: Optimizing Individual Choices to Reduce Risk". Environmental Health Perspectives. 113 (3): 266–271. doi:10.1289/ehp.7315. JSTOR 3436038. PMC 1253750. PMID 15743713.
  31. Dolbec, Julie; Mergler, Donna; Larribe, Fabrice; Roulet, Marc; Lebel, Jean; Lucotte, Marc (2001). "Sequential Analysis of Hair Mercury Levels in Relation to Fish Diet of an Amazonian Population, Brazil". Science of the Total Environment. 271 (1–3): 87–97. doi:10.1016/s0048-9697(00)00835-4. PMID 11346043. ProQuest 17890459.
  32. Yorifuji, Takashi (2011). "Long-Term Exposure to Methylmercury and Psychiatric Symptoms in Residents of Minamata, Japan". Environment International. 37 (5): 907–13. doi:10.1016/j.envint.2011.03.008. PMID 21470684. ProQuest 886085497.
  33. Mercury in the nation's streams: levels, trends, and implications Circular 1395By:Dennis A. Wentz, Mark E. Brigham, Lia C. Chasar, Michelle A. Lutz, and David P. Krabbenhoft
  34. Loring, Philip A.; Duffy, Lawrence K.; Murray, Maribeth S. (2010). "A Risk-Benefit Analysis of Wild Fish Consumption for Various Species in Alaska Reveals Shortcomings in Data and Monitoring Needs". Science of the Total Environment. 408 (20): 4532–41. doi:10.1016/j.scitotenv.2010.07.013. PMID 20673961.
  35. Al-Mughairi, Sabra; Yesudhason, P; Al-Busaidi, M; Al-Waili, A; Al-Rahbi, W. A.; Al-Mazrooei, N; Al-Habsi, S. H. (7 Nov 2013). "Concentration and Exposure Assessment of Mercury in Commercial Fish and Other Seafood Marketed in Oman". Journal of Food Science. 78 (7): T1082–90. doi:10.1111/1750-3841.12150. PMID 23701530.
  36. Loring, Philip A., and Lawrence K. Duffy, (2011) "Managing Environmental Risks: The Benefits of a Place-Based Approach." Remote and Rural Health, Vol. 11(3), p.1800, "Rural and Remote Health". Archived from the original on 2015-04-06. Retrieved 2015-03-05.
  37. Storelli, M. M. (2000). "Fish for Human Consumption: Risk of Contamination by Mercury". Food Additives and Contaminants. 17 (12): 1007–1011. doi:10.1080/02652030050207792. PMID 11271834. ProQuest 72558593.
  38. Trophic levels and maximum ages are, unless otherwise indicated, taken from the relevant species pages on Rainer Froese and Daniel Pauly (Eds) (2012) FishBase Archived 2012-11-29 at the Wayback Machine January 2012 version. Where a group has more than one species, the average of the principal commercial species is used
  39. Collins MA, Brickle P, Brown J and Belchier M (2010) "The Patagonian toothfish: biology, ecology and fishery" In: M Lesser (Ed.) Advances in Marine Biology, Volume 58, pp. 229–289, Academic Press. ISBN 978-0-12-381015-1.
  40. Lowerre-Barbieri, SK; Chittenden, ME; Barbieri, LR (1995). "Age and growth of weakfish, Cynoscion regalis, in the Chesapeake Bay region with a discussion of historical changes in maximum size". Fishery Bulletin. 93 (4): 643–656. Archived from the original on 2012-06-15. Retrieved 2012-01-09.
  41. "A bouillabaisse of fascinating facts about fish". NOAA: National Marine Fisheries Service. Archived from the original on October 21, 2009. Retrieved October 22, 2009.
  42. "Lessons from Minamata Disease and Mercury Management in Japan" (PDF). Ministry of Environment, Japan. September 2013. Archived (PDF) from the original on 14 October 2013. Retrieved 1 May 2014.
  43. Watanabe, C; Ser, P (2012). "Fish advisories in the USA and Japan: risk communication and public awareness of a common idea with different backgrounds" (PDF). Asia Pacific Journal of Clinical Nutrition. 21 (4): 487–494. PMID 23017306. Archived (PDF) from the original on 2014-04-20. Retrieved 18 Apr 2014.
  44. "Clean Air Mercury Rule". U.S. Environmental Protection Agency (EPA). 2005. Archived from the original on 2005-09-18.
  45. Kyle W. Danish, Britt Fleming, Stephen Fotis (2008-02-13). "D.C. Circuit Strikes Down EPA's Clean Air Mercury Rule". Washington, DC: Van Ness Feldman.CS1 maint: uses authors parameter (link)
  46. EPA (2012-02-16). "National Emission Standards for Hazardous Air Pollutants From Coal and Oil-Fired Electric Utility Steam Generating Units and Standards of Performance for Fossil-Fuel-Fired Electric Utility, Industrial-Commercial-Institutional, and Small Industrial-Commercial-Instituional Steam Generating Units; Final rule." Federal Register, 77 FR 9304
  47. "Cleaner Power Plants". Mercury and Air Toxics Standards. EPA. 2019-03-04.
  48. "Trump administration weakens mercury rule for coal plants". Reuters. 2020-04-16.
  49. Regulation (EU) 2017/852 of the European Parliament and of the Council of 17 May 2017 on mercury, and repealing Regulation (EC) No 1102/2008 (Text with EEA relevance. ), 2017-05-24, retrieved 2021-01-31
  50. Orgiazzi, A.; Ballabio, C.; Panagos, P.; Jones, A.; Fernández-Ugalde, O. (January 2018). "LUCAS Soil, the largest expandable soil dataset for Europe: a review: LUCAS Soil, pan-European open-access soil dataset". European Journal of Soil Science. 69 (1): 140–153. doi:10.1111/ejss.12499.
  51. Ballabio, Cristiano; Jiskra, Martin; Osterwalder, Stefan; Borrelli, Pasquale; Montanarella, Luca; Panagos, Panos (2021-05-01). "A spatial assessment of mercury content in the European Union topsoil". Science of The Total Environment. 769: 144755. doi:10.1016/j.scitotenv.2020.144755.
  52. Selin, N. E.; Selin, H. (2006). "Global Politics of Mercury Pollution: The Need for Multi-Scale Governance". Review of European Community & International Environmental Law. 15 (3): 258–269. doi:10.1111/j.1467-9388.2006.00529.x.
  53. "Declaration of the United Nations Conference on the Human Environment". Stockholm Convention. 1972. Archived from the original on 2015-03-14. Retrieved 18 Apr 2014.
  54. "Convention for the Prevention of Marine Pollution from Land-based Sources". Paris Convention. 1974. Archived from the original on 2014-05-07. Retrieved 18 Apr 2014.
  55. "Convention for the Prevention of Marine Pollution by Dumping from Ships and Aircraft". Oslo Convention. 1972. Archived from the original on 2014-11-02. Retrieved 18 Apr 2014.
  56. "Minamata Convention on Mercury". United States Environmental Protection Agency. 2013-07-29. Archived from the original on 2014-05-07. Retrieved 18 Apr 2014.
  57. "Mercury Study Report to Congress". EPA. 1997. Archived from the original on February 1, 2008. Retrieved January 23, 2008.
  58. "What You Need to Know About Mercury in Fish and Shellfish". FDA/EPA. March 2004. Archived from the original on March 21, 2004. Retrieved October 25, 2006.
  59. "Got Mercury? Online Calculator Helps Seafood Consumers Gauge Mercury Intake". Common Dreams. March 9, 2004. Archived from the original on April 19, 2009. Retrieved 2008-03-30.
  60. "FDA tests show risk in tuna". Chicago Tribune. January 27, 2006. Retrieved 2007-05-01.
  61. Balshaw, S.; Edwards, J.W.; Ross, K.E.; Daughtry, B.J. (December 2008). "Mercury distribution in the muscular tissue of farmed southern bluefin tuna (Thunnus maccoyii) is inversely related to the lipid content of tissues". Food Chemistry. 111 (3): 616–621. doi:10.1016/j.foodchem.2008.04.041.
  62. "NRDC: Mercury Contamination in Fish - Guide to Mercury in Sushi". Archived from the original on 2009-04-21.
  63. "What You Need to Know About Mercury in Fish and Shellfish". fda.gov. Archived from the original on 18 January 2017. Retrieved 1 May 2018.
  64. Nicholas V.C. Ralstona; Carla R. Ralstona; J. Lloyd Blackwell III; Laura J. Raymonda (Sep 2008). "Dietary and tissue selenium in relation to methylmercury toxicity" (PDF). Neurotoxicology. 29 (5): 802–11. CiteSeerX 10.1.1.549.3878. doi:10.1016/j.neuro.2008.07.007. PMID 18761370. Archived (PDF) from the original on 2012-07-24. Retrieved 2012-08-23.
  65. Scientific Opinion on the risk for public health related to the presence of mercury and methylmercury in food Archived 2013-08-12 at the Wayback Machine EFSA Journal 2012;10(12):2985 [241 pp.]. Retrieved 04/24/2013

Additional sources

This article is issued from Wikipedia. The text is licensed under Creative Commons - Attribution - Sharealike. Additional terms may apply for the media files.