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National Atmospheric Deposition Program

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The National Atmospheric Deposition Program (NADP) is a Cooperative Research Support Program of the State Agricultural Experiment Stations (NRSP-3). Housed at the Wisconsin State Laboratory of Hygiene at the University of Wisconsin–Madison , the NADP is a collaborative effort between many different groups, such as: Federal, state, tribal, local governmental agencies, educational institutions, private companies, and non-governmental agencies. These organizations work together in order to operate monitoring sites and report deposition data. The NADP provides free access to all of its data, including seasonal and annual averages, trend plots, deposition maps, reports, manuals, and educational brochures.

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76-533: The National Atmospheric Deposition Program, or NADP, was initiated by the State Agricultural Experiment Station in 1977 to monitor the effects of atmospheric deposition on crops, rangelands, forests, surface waters, and other natural and cultural resources. The initial goal was to provide regional data for the deposition of acids, nutrients, and base cations (including temporal trends/amounts and geographic distributions). In 1978,

152-611: A fertilizer in the environment and alter the competitive interactions of plants, thereby favoring the growth of some plant species and inhibiting others, potentially leading to changes in species composition and abundance . The deposition of nitrogen contributes to nutrient enrichment in freshwater, coastal, and estuarine ecosystems, which may cause toxic algal blooms , fish kills, and loss of biodiversity . Air pollutants impact essential ecosystem services such as air and water purification, decomposition and detoxification of waste materials, and climate regulation. When deposition

228-554: A half-life in human blood of about 50 days. Several studies indicate that methylmercury is linked to subtle developmental deficits in children exposed in utero such as loss of IQ points, and decreased performance in tests of language skills, memory function and attention deficits. Methylmercury exposure in adults has also been linked to increased risk of cardiovascular disease including heart attack . Some evidence also suggests that methylmercury can cause autoimmune effects in sensitive individuals. Despite some concerns about

304-432: A steady-state concept and that it therefore includes no information whatsoever regarding how long it takes before effects are visible. A simplified illustration of dynamic aspects is the target load function, which is the load at which the chemical criterion recovers before a chosen year, the target year. Thus, for target years in the near future the target load function is lower than the critical load and for target years in

380-495: A balanced, stable, and ongoing program. There are eight voting members, as well as numerous non-voting members, that make decisions and appoint responsibilities to the subcommittees. The two standing Technical Subcommittees, Education and Outreach Subcommittee (EOS) (formally the Ecological Response and Outreach Subcommittee) and Network Operations Subcommittee (NOS), provide the technical support necessary to promote

456-880: A broad multi-agency/entity audience, fill gaps in critical loads development in the U.S., provide consistency in development and use of critical loads in the U.S., and promote understanding of critical loads approaches through development of outreach and communications materials. Federal Land Managers, such as the National Park Service Archived 2017-03-30 at the Wayback Machine , U.S. Forest Service , and U.S. Fish and Wildlife Service , use critical loads to: identify resources at risk, focus research and monitoring efforts, inform planning and other land management activities, evaluate potential impacts of emission increases, and develop pollution reduction strategies. The U.S. Environmental Protection Agency

532-420: A comprehensive set of global measurements, the ocean contains about 60,000 to 80,000 tons of mercury from pollution, and mercury levels in the upper ocean have tripled since the beginning of the industrial revolution. Higher mercury levels in shallower ocean waters could increase the amount of the toxicant accumulating in food fish, exposing people to a greater risk of mercury poisoning. Critical load In

608-460: A forested landscape. The importance of litterfall mercury data for quantifying atmospheric mercury deposition to forests was demonstrated with studies at NADP sites in the eastern USA from 2007-2009 and 2007 to 2014.   The AIRMoN sites were primarily used to assess the impacts of emission changes such as potential effects from new sources, federal Clean Air Act controls, and source-receptor relationships in atmospheric models. The network measured

684-450: A given species of fish, older and larger fish have higher levels of methylmercury than smaller fish. Fish that develop in water bodies that are more acidic also tend to have higher levels of methylmercury. Ingested methylmercury is readily and completely absorbed by the gastrointestinal tract . It is mostly found complexed with free cysteine and with proteins and peptides containing that amino acid. The methylmercuric-cysteinyl complex

760-830: A good source of nutrition and has significant health benefits, but that consumers, in particular pregnant women, women of child-bearing age, nursing mothers, and young children, should avoid fish with high levels of methylmercury, limit their intake of fish with moderate levels of methylmercury, and consume fish with low levels of methylmercury no more than twice a week. In recent years, there has been increasing recognition that methylmercury affects fish and wildlife health, both in acutely polluted ecosystems and ecosystems with modest methylmercury levels. Two reviews document numerous studies of diminished reproductive success of fish, fish-eating birds, and mammals due to methylmercury contamination in aquatic ecosystems. Reported methylmercury levels in fish, along with fish consumption advisories, have

836-476: A result of mercury released from the mercury-cell Chloralkali process , which uses liquid mercury as an electrode in a process that entails electrolytic decomposition of brine, followed by mercury methylation in the aquatic environment. An acute methylmercury poisoning tragedy occurred also in Minamata, Japan , following release of methylmercury into Minamata Bay and its tributaries (see Minamata disease ). In

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912-729: A series of critical loads workshops from 2003 to 2005 and an ad hoc committee established in 2006, national efforts were unified through the development of the Critical Loads of Atmospheric Deposition ( CLAD ) Science Committee as part of the National Atmospheric Deposition Program ( NADP ). CLAD is a multi-agency group consisting of federal and state government agencies, non-governmental organizations, environmental research organizations, and universities. The goals of CLAD are to: facilitate sharing of technical information on critical loads topics within

988-449: A two-week period via a Radiello®-passive sampler, which is a simple diffusive sampler that offers higher capacity and faster sampling rates than other devices. Therefore, AMoN can provide reliable data to aid in meeting air quality policies and administration needs. AMoN collects data biweekly to determine the spatial variability and seasonality of ammonia concentrations. The MLN can provide an important component of mercury dry deposition to

1064-437: A weekly basis (methyl mercury is measured monthly at some sites), which provides wet deposition data for surface waters and other waterways. The goal is to deliver accurate information that allows researchers to evaluate the linkage between mercury and health, which is strengthened by its large spatial and temporal footprint.  The AMNet consists of approximately 15 sites across the U.S. and Canada. The function of these sites

1140-405: Is an organometallic cation with the formula [CH 3 Hg] . It is the simplest organomercury compound. Methylmercury is extremely toxic, and its derivatives are the major source of organic mercury for humans. It is a bioaccumulative environmental toxicant with a 50-day half-life . Methylmercury is the causative agent of the infamous Minamata disease . "Methylmercury" is a shorthand for

1216-399: Is called the critical load and the difference between the current deposition level and the critical load is called exceedance. In the early days, critical loads were often calculated as a single value, e.g. critical load of acidity. Today a two-dimensional critical load function is often calculated, with the x-axis as N-deposition and the y-axis as S-deposition. The critical loads concept is

1292-523: Is currently focused on more subtle effects that may be linked to levels of exposure presently seen in populations with high to moderate levels of dietary fish consumption. These effects are not necessarily identifiable on an individual level or may not be uniquely recognizable as due to methylmercury. However, such effects may be detected by comparing populations with different levels of exposure. There are isolated reports of various clinical health effects in individuals who consume large amounts of fish; however,

1368-834: Is expanding use of critical loads for assessments and policy development, including consideration of critical loads when setting National Ambient Air Quality Standards . The U.S. has adopted two approaches for creating critical loads: empirical and steady-state mass balance critical loads. Empirical critical loads are derived based on observations of ecosystem responses (such as changes in plant diversity, soil nutrient levels, or fish health) to specific deposition levels. These relationships are created using dose-response studies or by measuring ecosystem responses to increasing gradients of deposition over space or time. Steady-state mass balance critical loads are derived from mathematical mass-balance models under assumed or modeled equilibrium conditions. A steady-state condition may be achieved far into

1444-779: Is formed from inorganic mercury by the action of microbes that live in aquatic systems including lakes , rivers , wetlands , sediments , soils and the open ocean . This methylmercury production has been primarily attributed to anaerobic bacteria in the sediment. Capable bacteria that can methylate mercury are mostly the sulfate-reducing bacteria (SRB), iron-reducing bacteria (FeRB) and methanogens . Significant concentrations of methylmercury in ocean water columns are strongly associated with nutrients and organic matter remineralization , which indicate that remineralization may contribute to methylmercury production. Direct measurements of methylmercury production using stable mercury isotopes have also been observed in marine waters, but

1520-739: Is greater than the critical load of a pollutant for a particular location, it is considered a critical load exceedance, meaning the biota are at increased risk of ecological harm. Some components of an ecosystem are more sensitive to deposition than others; therefore, critical loads can be developed for a variety of ecosystem components and responses, including (but not limited to) shifts in diatoms, increases in invasive grass species, changes in soil chemistry, decreased forest health, altered and reduced biodiversity, and lake and stream acidification. The history, terminology, and approach used to calculate critical loads differ by region and country. The differences between approaches used by European countries and in

1596-466: Is of the utmost importance to the NADP. This is accomplished, in part, by ensuring that all sites adhere to specific standard operating procedures. This provides consistent methodology at all sites within the networks. The SOPs can be viewed here: a.    SAESD (State Agricultural Experiment Station Directors). 2013. Guidelines for Multistate Research Activities. Developed by SAESD in cooperation with

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1672-597: Is only a trace constituent of such fuels, their large scale combustion in utility and commercial/industrial boilers in the United States alone results in release of some 80.2 tons (73 metric tons ) of elemental mercury to the atmosphere each year, out of total anthropogenic mercury emissions in the United States of 158 tons (144 metric tons)/year. In the past, methylmercury was produced directly and indirectly as part of several industrial processes such as

1748-541: Is organized through an Executive Committee, Technical Subcommittees, several advisory subcommittees, science subcommittees, and ad hoc groups. The second group is Program Operations , which is managed by a professional staff housed at the Wisconsin State Laboratory of Hygiene at the University of Wisconsin-Madison. The Program Office oversees day to day tasks, including coordinating with

1824-423: Is recognized by amino acids transporting proteins in the body as methionine , another essential amino acid . Because of this mimicry, it is transported freely throughout the body including across the blood–brain barrier and across the placenta , where it is absorbed by the developing fetus . Also for this reason as well as its strong binding to proteins, methylmercury is not readily eliminated. Methylmercury has

1900-492: Is to link the status of that element to some chemical criterion (e.g. the base cation to aluminium ratio, Bc/Al) and a critical limit (e.g. Bc/Al=1) which should not be violated. Finally, a mathematical model (e.g. the Simple Mass Balance model, SMB) needs to be created so that the deposition levels that result in the chemical criterion reaching exactly the critical limit can be calculated. That deposition level

1976-536: Is to measure ambient air concentrations of gaseous oxidized mercury (GOM), particulate bound mercury (PBM 2.5 ), and gaseous elemental mercury (GEM). This network works to monitor and report atmospheric mercury that causes dry and total deposition of mercury at select MDN sites. AMNet produces high-resolution data to determine atmospheric mercury trends and models, the ecological consequences of mercury discharging sources, and how to adequately control mercury levels. The AMoN measures ambient ammonia gas concentrations over

2052-640: The U.S. Fish & Wildlife Service , the Bureau of Land Management , the U.S. Forest Service , the U.S. Department of Agriculture - Agricultural Research Service , the National Science Foundation , and the U.S. Department of Energy . The NTN has over 250 sites that focus on wet deposition chemistry by collecting weekly precipitation samples nationwide. The samples are sent to the NADP Analytical Laboratory (NAL) at

2128-449: The atmosphere , they are subsequently deposited into ecosystems . Both sulfur and nitrogen deposition can acidify surface waters and soils . As added acidity lowers the pH of water, fish and invertebrate health are negatively impacted. Sulfur and nitrogen, as acidifying agents, may change soil nutrient content by removing calcium and releasing toxic aluminum, further impacting plants and animals. Nitrogen deposition can also act as

2204-628: The 1980s, culminated in Title IV of the 1990 Clean Air Act Amendments (CAAA), also known as the Acid Deposition Control Program. Title IX of the CAAA reauthorized NAPAP to conduct acid rain research and monitoring, and to periodically assess the costs, benefits, and effectiveness of Title IV. The NAPAP member agencies were the U.S. Environmental Protection Agency, the U.S. Department of Energy, the U.S. Department of Agriculture,

2280-635: The BAC is to advise the EC with suggestions pertaining to the budget, and to outline financial planning for current and future years. The QAAG is in charge of ensuring quality management in all aspects of NADP, including the Program Office, networks, and laboratories. To do so, they provide recommendations for manuals and procedures to the EC. The DMAG counsels the EC in data management by reviewing data reports and formats in order to ensure that they are in line with

2356-581: The CAAA were implemented. The NAPAP officially ended with publication of the last report in 2011. To reflect the federal NAPAP role in the NADP, the network name was changed to NADP National Trends Network (NTN) The organizational structure of the NADP follows the State Agricultural Experiment Station Guidelines for Multi-State Research Activities (SAESD, 2006). This framework allows any individual or institution to participate in any segment of NADP, whether it be

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2432-594: The Cooperative State Research, Education, and Extension Service, USDA (NIFA) and the Experiment Station Committee on Organization and Policy (ESCOP). Approved September 26, 2000, updated August 15, 2013. http://escop.ncsu.edu/docs/MRF Guidelines Revised 08 1 513.pdf b.     NADP Governance Handbook c.     https://nadp.slh.wisc.edu/ Methyl mercury Methylmercury (sometimes methyl mercury )

2508-510: The EC in 2010 and 2011, respectively. The goal of the CLAD is to provide a forum, across all levels of government and industry, that encourages the use and discussion of technical information and critical load science. TDep seeks to evaluate pressing issues of atmospheric deposition via a collaboration between a wide range of groups. TDep also aims to improve the ability to measure and model wet and dry deposition. To do so, they are working to advance

2584-669: The Executive Committee, the individual monitoring networks, the analytical laboratories, the External Quality Assurance Program, and the Network Equipment Depot. The NADP is governed by an elected and rotating Executive Committee (8 members). Currently, there are two standing Subcommittees, three standing Advisory Committees, and four Science Committees (highlighted below) that contribute continuous, scheduled suggestions to

2660-415: The Executive Committee. Ad hoc groups and the Program Office also supply crucial input to the Executive Committee. The Executive Committee (EC) is responsible for considering and, if approved, executing decisions which are often based on the suggestions made by the subcommittees, advisory committees, science committees, and ad hoc groups. In addition, the EC is accountable for financial decisions and securing

2736-619: The Mercury in the Environment and Links to Deposition Science Committee (MELD), was formed in 2020 to improve our understanding of atmospherically-derived mercury sources, pathways, processes, and effects on the environment. All NADP operations are administered at the NADP Program Office, which is currently located at the Wisconsin State Laboratory of Hygiene at the University of Wisconsin–Madison. The five main functions of

2812-636: The NADP established an additional two networks in the 1990s: The Atmospheric Integrated Research Monitoring Network (AIRMoN), which collected daily samples at five sites, and the Mercury Deposition Network (MDN), which has more than 80 sites (six of which are located in Canada). The MDN collects wet deposition data for both total and methyl mercury in precipitation. In 2009, the Atmospheric Mercury Network (AMNet)

2888-627: The NADP: Private companies and other non-governmental organizations, universities, local and state government agencies (i.e. state agricultural experiment stations ), national laboratories, Native American environmental organizations, Canadian government agencies , the National Oceanic and Atmospheric Administration , the U.S. Environmental Protection Agency , the U.S. Geological Survey , the National Park Service ,

2964-696: The NTN and AMoN networks, and the Mercury (Hg) Analytical Laboratory (HAL). The HAL was previously housed at Eurofins Frontier Global Sciences, Inc. in Bothell, Washington. In May 2023, the CAL and the HAL were renamed the NADP Analytical Laboratory (NAL). In addition, the Network Equipment Depot, located at the WSLH, provides spare parts for NADP field equipment and troubleshoots site operation problems. More than 80 sponsors support

3040-600: The Ontario case, inorganic mercury discharged into the environment was methylated in the environment; whereas, in Minamata, Japan, there was direct industrial discharge of methylmercury. Because methylmercury is formed in aquatic systems, and because it is not readily eliminated from organisms, it is biomagnified in aquatic food chains from bacteria , to plankton , through macroinvertebrates , to herbivorous fish and to piscivorous (fish-eating) fish. At each step in

3116-447: The Program Office are network administration, management, meetings and trainings, data and publications, and quality assurance and management. Network administration involves overseeing the endeavors of all five networks, managing sample analysis, and coordinating data storage and user availability. These functions are executed from the two analytical laboratories housed at WSLH: The Central Analytical Lab (CAL), which analyses samples from

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3192-574: The U.S. Department of Interior, the National Aeronautics and Space Administration, and the National Oceanic and Atmospheric Administration. The NAPAP published a total of four reports: 1991 (multiple volumes), 1998, 2005, and 2011. The Program was able to describe and document strong reductions in sulfur dioxide and nitrogen oxide emissions, as well as the resulting atmospheric deposition from 1980 to 2010 as various elements of

3268-467: The U.S. are discussed below. In European countries, critical loads and the similar concept of critical levels have been used extensively within the 1979 UN-ECE Convention on Long-Range Transboundary Air Pollution . As an example the 1999 Gothenburg protocol to the LRTAP convention takes into account acidification (of surface waters and soils ), eutrophication of soils and ground-level ozone and

3344-470: The United Nations Food and Agriculture Organization (FAO), have issued guidance for fish consumers that is designed to limit methylmercury exposure from fish consumption. At present, most of this guidance is based on protection of the developing fetus; future guidance, however, may also address cardiovascular risk. In general, fish consumption advice attempts to convey the message that fish is

3420-673: The Wisconsin State Lab of Hygiene for analysis and are then used to determine geographic distribution and annual trends. The sample collection and handling methods follow strict clean-handling procedures in order to ensure accurate results. The analytes monitored are: Free acidity (H as pH), conductance, calcium (Ca), magnesium (Mg), sodium (Na), potassium (K), sulfate (SO 4 ), nitrate (NO 3 ), chloride (Cl), and ammonium (NH 4 ). The NAL also measures orthophosphate, but only for quality assurance as an indicator of sample contamination. The MDN measures total mercury concentrations on

3496-545: The actual critical load, experimental studies may fail to quantify the critical loads because substantial ecosystem changes had already occurred. Moreover, the values of the critical loads can vary remarkably when based on different biological or chemical response of an ecosystem, such as physiological variation, reduced biodiversity, elevated nitrate leaching, and changes in soil microorganisms. Empirical critical loads have been assessed for some forests and grasslands in China, but

3572-493: The correct protocols. The science committees do not directly advise NADP networks, but they are closely affiliated. They assess major atmospheric deposition concerns and track scientific interest and participation. The first scientific committee was the Critical Loads of Atmospheric Deposition (CLAD), and the second was the Total Deposition Science Committee (TDep). CLAD and TDep were approved by

3648-716: The deposition levels with reported field occurrence of detrimental ecological effects. The steady-state mass balance model calculates the critical load of an ecosystem over the long-term by defining acceptable values for elements leaching out of the ecosystem. Although empirical nitrogen critical loads have been well summarized for Europe and the United States, large uncertainties still exist in Asia due to very limited and short-term experimental studies by using relatively high levels of nitrogen application. In regions (e.g., eastern and southern China) where historical nitrogen deposition has already been very high and perhaps even higher than

3724-524: The distant future the target load function approaches the critical load function. Calculating critical load functions and target load functions include several simplifications and thus can be viewed as a risk concept: The higher the exceedance the higher the risk for adverse effects and there is a certain risk that zero exceedance will still lead to adverse effects. In the U.S., while various entities were discussing critical loads prior to 2000, efforts were independent and disjointed. However, in 2010, following

3800-411: The distributed mercury depositional input is from current anthropogenic sources, and 70% is from natural sources. The natural sources category includes re-emission of mercury previously deposited from anthropogenic sources. According to one study, based on modeled concentrations, pre- Anthropocene tissue-bound levels in freshwater fish may not have differed markedly from current levels. However, based on

3876-558: The dumping of industrial waste that resulted in the pollution and subsequent mass poisoning in Minamata and Niigata , Japan and the situation in Iraq in the 1960s and 1970s in which wheat treated with methylmercury as a preservative and intended as seed grain was fed to animals and directly consumed by people (see Basra poison grain disaster ). These episodes resulted in neurological symptoms including paresthesias , loss of physical coordination, difficulty in speech , narrowing of

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3952-462: The emissions of sulfur dioxide , ammonia , nitrogen oxide and non-methane volatile organic compounds (NMVOCs). For acidification and eutrophication the critical loads concept was used, whereas for ground-level ozone the critical levels were used instead. To calculate a critical load, the target ecosystem must first be defined and in that ecosystem (e.g. a forest ) a sensitive "element" must be identified (e.g. forest growth rate). The next step

4028-676: The first NADP sites began collecting weekly precipitation samples. In the early 1980s, the National Acid Precipitation Assessment Program (NAPAP) was established, and began to work in collaboration with NADP in order to sustain a long term, quality-assured precipitation monitoring network. This unification brought on a major expansion as well as newfound federal agency support. Today, the NADP National Trends Network (NTN) has more than 250 sites. In response to emerging issues,

4104-528: The food chain, the concentration of methylmercury in the organism increases. The concentration of methylmercury in the top-level aquatic predators can reach a level a million times higher than the level in the water. This is because methylmercury has a half-life of about 72 days in aquatic organisms resulting in its bioaccumulation within these food chains. Organisms, including humans, fish-eating birds, and fish-eating mammals such as otters and cetaceans (i.e. whales and dolphins ) that consume fish from

4180-410: The future. The models used to determine steady-state critical loads vary in complexity with regard to process representation but can include water and soil chemistry, mineral soil weathering rates, deposition data, and ecological response data. In Asia, both empirical and steady-state mass balance approaches have been used to estimate critical loads. Empirical critical loads were simply determined as

4256-404: The goals of NADP. EOS maintains a platform to coordinate outreach and education activities among the network and scientific subcommittees. With approval and recommendation from the Executive Committee, EOS will provide guidance for outreach efforts and educational materials to the Program Office. EOS will provide a forum to enable communication of outreach and education needs, goals and activities of

4332-431: The hypothetical "methylmercury cation", sometimes written methylmercury(1+) cation or methylmercury(II) cation . This functional group is composed of a methyl group bonded to an atom of mercury . Its chemical formula is CH 3 Hg (sometimes written as MeHg ).The Methylmercury compound has an overall charge of +1, with Hg in the +2 oxidation state . Methylmercury exists as a substituent in many complexes of

4408-700: The manufacture of acetaldehyde . However, currently there are few direct anthropogenic sources of methylmercury pollution in the United States. Whole-lake ecosystem experiments at IISD-ELA in Ontario , Canada, showed that mercury falling directly on a lake had the fastest impacts on aquatic ecosystems as opposed to mercury falling on the surrounding land. This inorganic mercury is converted to methylmercury by bacteria. Different stable isotopes of mercury were added to lakes, wetlands , and uplands , simulating rain, and then mercury concentrations in fish were analyzed to find their source. The mercury applied to lakes

4484-493: The microbes involved are still unknown. Increased methylmercury concentrations in water and fish have been detected after flooding of soils associated with reservoir creation (e.g. for hydroelectric power generation ) and in thermokarst wetlands that form after permafrost thaw. The increased methylmercury concentration is due to its ability to bio-accumulate and biο-magnify in aquatic food webs. There are various sources of inorganic mercury that may indirectly contribute to

4560-401: The monitoring or the research aspect of atmospheric deposition. NADP is managed by two groups. The first being Program Management , which is largely a volunteer group made up of site sponsors and supervisors, policy experts from several agencies (at the federal, state, and local levels), scientists and research specialists, and anyone with an interest in atmospheric deposition. Program management

4636-519: The potential to disrupt people's eating habits, fishing traditions, and the livelihoods of the people involved in the capture, distribution, and preparation of fish as a foodstuff for humans. Furthermore, proposed limits on mercury emissions have the potential to add costly pollution controls on coal-fired utility boilers. Nevertheless, substantial benefits can be achieved globally by introducing mercury emission reduction measures because they reduce human and wildlife exposure to methylmercury. About 30% of

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4712-419: The production of methylmercury from microbes in the environment. Natural sources of mercury released to the atmosphere include volcanoes , forest fires , volatilization from the ocean and weathering of mercury-bearing rocks . Anthropogenic sources of mercury include the burning of wastes containing inorganic mercury and from the burning of fossil fuels , particularly coal . Although inorganic mercury

4788-718: The relationship between methylmercury exposure and autism, there are few data that support such a link. Although there is no doubt that methylmercury is toxic in several respects, including through exposure of the developing fetus, there is still some controversy as to the levels of methylmercury in the diet that can result in adverse effects. Recent evidence suggests that the developmental and cardiovascular toxicity of methylmercury may be mitigated by co-exposures to omega-3 fatty acids and perhaps selenium , both found in fish and elsewhere. There have been several episodes in which large numbers of people were severely poisoned by food contaminated with high levels of methylmercury, notably

4864-648: The same contaminants as the NTN, but sampling occurred daily during precipitation to provide greater temporal resolution. This consistent, high-resolution sampling improved the researchers’ ability to evaluate the data and, therefore, provide reliable results. The network was discontinued in September 2019. Brochures Annual Data Summaries Quality Assurance Reports CLAD Science Committee Reports TDep Science Committee Reports AMSC Study Plan MELD Science Committee Reports Accurate and consistent measurement of gases and deposition at every monitoring site

4940-748: The specific health effects and exposure patterns have not been verified with larger, controlled studies. Many governmental agencies, the most notable ones being the United States Environmental Protection Agency (EPA), the United States Food and Drug Administration (FDA), Health Canada , and the European Union Health and Consumer Protection Directorate-General , as well as the World Health Organization (WHO) and

5016-613: The steady-state mass balance approach. Thereafter, critical loads with higher resolution were calculated in many Asian countries such as Japan, Russia, South Korea, India, and China. Although similar methods were applied in Asia as in Europe, the steady state mass balance approach has been improved by considering base cation deposition. Steady-state mass balance critical loads have been used to designate Acid Rain Control Zones and Sulphur Dioxide Pollution Control Zones in China. In

5092-415: The study of air pollution , a critical load is defined as "a quantitative estimate of an exposure to one or more pollutants below which significant harmful effects on specified sensitive elements of the environment do not occur according to present knowledge". Air pollution research in relation to critical loads has focused on nitrogen and sulfur pollutants. After these pollutants are emitted into

5168-504: The subcommittees and networks. The goal is to enhance efficiency in messaging and reaching new audiences. The NOS focuses on equipment, research, sampling methods, collection sites, and the evaluation of the issues that arise from these components. The three advisory subcommittees include the Budget Advisory Committee (BAC), Quality Assurance Advisory Group (QAAG), and Data Management Advisory Group (DMAG). The role of

5244-562: The techniques and procedures which are used to estimate deposition of sulfur, nitrogen, and mercury. In October 2017, the Aeroallergen Monitoring Science Committee (AMSC) was added as the third science committee. AMSC seeks to utilize emerging technologies to advance the science of aeroallergen monitoring, enhance the understanding of quality data collection and evaluation methods, and provide lasting data for national networks. A fourth science committee,

5320-647: The top of the aquatic food chain receive the methylmercury that has accumulated through this process, plus the toxins in their habitat. Fish and other aquatic species are the main source of human methylmercury exposure. The concentration of mercury in any given fish depends on the species of fish, the age and size of the fish and the type of water body in which it is found. In general, fish-eating fish such as shark , swordfish , marlin , larger species of tuna , walleye , largemouth bass , and northern pike , have higher levels of methylmercury than herbivorous fish or smaller fish such as tilapia and herring . Within

5396-455: The type [MeHgL] (L = Lewis base) and MeHgX (X = anion). As a positively charged ion, it readily combines with anions such as chloride ( Cl ), hydroxide ( OH ) and nitrate ( NO − 3 ). It has particular affinity for sulfur -containing anions, particularly thiols ( RS ). Thiols are generated when the amino acid cysteine and the peptide glutathione form strong complexes with methylmercury: Methylmercury

5472-688: The values for many other ecosystems remain unassessed. With more emerging field experiments, critical loads will be better estimated in the near future. In South and East Asia, comprising China, Korea, Japan, the Philippines, Indo-China, Indonesia, and the Indian subcontinent, critical loads were first computed and mapped as part of the impact module of the Asian version of the Regional Air pollution INformation and Simulation model (RAINS-Asia) based on

5548-406: The visual field , hearing impairment , blindness , and death. Children who had been exposed in utero through their mothers' ingestion were also affected with a range of symptoms including motor difficulties, sensory problems and intellectual disability . At present, exposures of this magnitude are rarely seen and are confined to isolated incidents. Accordingly, concern over methylmercury pollution

5624-460: Was approved as the sixth network in 2021 with 22 sites. MLN provides estimates of mercury dry deposition in forested landscapes using passive collectors.  The National Acid Precipitation Assessment Program (NAPAP) was a cooperative federal program that was first authorized in 1981 in order to coordinate acid rain research and report those findings to the U.S. Congress. The research, monitoring, and assessment efforts of NAPAP, and other groups in

5700-522: Was formed as a fourth network, and as a subset of some MDN sites. The network uses continuous automatic measurement systems to monitor gaseous and particulate concentrations of atmospheric mercury. The Ammonia Monitoring Network (AMoN) was added as a fifth network in October 2010, and it currently has more than 100 sites. AMoN monitors ammonia gas concentrations across the United States to provide consistent and lasting data. The Mercury Litterfall Network (MLN)

5776-489: Was found in young-of-the-year yellow perch within two months, whereas the mercury applied to wetlands and uplands had a slower but longer influx. Acute methylmercury poisoning can occur either directly from the release of methylmercury into the environment or indirectly from the release of inorganic mercury that is subsequently methylated in the environment. For example, methylmercury poisoning occurred at Grassy Narrows in Ontario, Canada (see Ontario Minamata disease ), as

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