Technical Factsheet on: MERCURY
List of Contaminants
As part of the Drinking Water and Health pages, this fact sheet is part of a larger publication:
National Primary Drinking Water Regulations
Drinking Water Standards
MCLG: 0.002 mg/L
MCL: 0.002 mg/L
HAL(child): none
Health Effects Summary
Acute: EPA has found mercury to potentially cause kidney damage from short-term exposures at
levels above the MCL. No Health Advisories have been established for short-term exposures.
Chronic: Mercury has the potential to cause kidney damage from long-term exposure at levels
above the MCL.
Cancer: There is inadequate evidence to state whether or not mercury has the potential to cause
cancer from lifetime exposures in drinking water.
Usage Patterns
Nearly 8 million lbs. of mercury were produced in the U.S. in 1986.
Electrical products such as dry-cell batteries, fluorescent light bulbs, switches, and other control
equipment account for 50% of mercury used. Mercury is also used in substantial quantities in
electrolytic preparation of chlorine and caustic soda (chlor-alkali industry, mercury cell process;
25%), paint manufacture (12%), and dental preparations (3%). Lesser quantities are used in
industrial catalyst manufacture (2%), pesticides manufacture (1%), general laboratory use (1%),
and pharmaceuticals (0.1%).
Release Patterns
A joint FAO/WHO expert committee on Food Additives in 1972 quotes the major source of
mercury as the natural degassing of the earth's crust in the range of 25,000-150,000 ton of Hg/yr.
Twenty thousand tons of mercury are also released into the environment each year by human
activities such as combustion of fossil fuels and other industrial release. Anthropogenic sources
of airborne mercury (Hg) may arise from the operation of metal smelters or cement manufacture.
Water borne pollution may originate in sewage, metal refining operations, or most notably, from
chloralkali plants. In general, industrial and domestic products, such as thermometers, batteries,
and electrical switches which account for a significant loss of mercury to the environment,
ultimately become solid waste in major urban areas.
From 1987 to 1993, according to EPA's Toxic Chemical Release Inventory, mercury releases to
land and water totalled nearly 68,000 lbs., of which 90 percent was to land. These releases were
primarily from chemical and allied industries. The largest releases occurred in Tennessee and
Louisiana. The largest direct releases to water occurred in West Virginia and Alabama.
Environmental Fate
Two characteristics, volatility and biotransformation, make mercury somewhat unique as an
environmental toxicant. Its volatility accounts for atmospheric concentrations up to 4 times the
level of contaminated soils in an area. Inorganic forms of mercury (Hg) can be converted to
organic forms by microbial action in the biosphere.
In aquatic systems, mercury appears to bind to dissolved matter or fine particulates, while the
transport of mercury bound to dust particles in the atmosphere or bed sediment particles in rivers
and lakes is generally less substantial. The conversion, in aquatic environments, of inorganic
mercury compounds to methyl mercury implies that recycling of mercury from sediment to water
to air and back could be a rapid process. In a study of mercury elimination from wastewater, 47%
of added mercury was removed in presence of a Pseudomonas strain. Uptake of mercury was
severely inhibited by sodium chloride, sodium sulfate, and mono- and dibasic potassium
phosphate.
In the atmosphere, 50% of the volatile form is mercury (Hg) vapor with sizeable portion of
remainder being Hg(II) and methylmercury, 25 to 50% of Hg in water is organic. Hg in the
environment is deposited and revolatilized many times, with a residence time in the atmosphere
of at least a few days. In the volatile phase it can be transported hundreds of kilometers.
Bioconcentration factors of 63,000 for freshwater fish, 10,000 for salt water fish, 100,000 for
marine invertebrates, and 1000 for freshwater and marine plants have been found. As the tissue
concentration approaches steady-state, net accumulation rate is slowed either by a reduction in
uptake rate, possibly due to inhibition of membrane transport, or by an increase in depuration
rate, possibly because of a saturation of storage sites, or both. Acidification of a body of water
might also increase mercury residues in fish even if no new input of mercury occurs, possibly
because lower pH increases ventilation rate and membrane permeability, accelerates the rates of
methylation and uptake, affects partitioning between sediment and water, or reduces growth or
reproduction of fish.
Chemical/Physical Properties
CAS Number: 7439-97-6
Color/ Form/Odor: Silver-white, heavy, mobile, liquid metal. Solid mercury is
tin-white. Odorless
M.P.: -38.87 C B.P.: 356.7 C
Vapor Pressure: 2x10-3 mm Hg at 25 C
Density/Spec. Grav.: 13.5 at 25 C
Solubility: 0.06 g/L of water at 25 C; Slightly soluble in water
Soil sorption coefficient: N/A
Odor/Taste Thresholds: N/A
Bioconcentration Factor: Bioconcentration factors of 63,000 for freshwater
and 10,000 for salt water fishes. BCFs of 100,000 for invertebrates.
Henry's Law Coefficient: N/A; volatilization from water and soil is
significant
Synonyms/Ores: Liquid silver, Quicksilver, Hydragyrum, Colloidial mercury.
Important commercial ore is cinnabar, but also found in limestone, calcareous
shales, sandstone, serpentine, chert andesite and others.
Other Regulatory Information
Monitoring:
-- For Ground Water Sources:
Initial Frequency-1 sample once every 3 years
Repeat Frequency-If no detections for 3 rounds, once every 9 years
-- For Surface Water Sources:
Initial Frequency-1 sample annually
Repeat Frequency-If no detections for 3 rounds, once every 9 years
-- Triggers - If detect at > 0.002 mg/L, sample quarterly.
Analysis
| Reference Source | Method Number |
| EPA 600/4-79-020 | 245.1; 245.2 |
| Standard Methods | 303F |
Treatment/Best Available Technologies: Coagulation/Filtration*; Granular Activated Carbon;
Lime softening*; Reverse osmosis*
* These treatments are recommended only if influent Hg concentrations do not exceed 10 ug/L
Toxic Release Inventory - Releases to Water and Land, 1987 to 1993 (in pounds):
| | Water | Land |
| TOTALS | 6,971 | 60,877 |
| Top Six States |
|---|
|
TN | 164 | 29,161
| |
LA | 431 | 21,829
| |
DE | 117 | 3,860
| |
OH | 29 | 2,760
| |
AL | 1,462 | 4,001
| |
WV | 1,657 | 454
|
| Major Industries* |
|---|
|
Chemical, allied products | 12,269 | 74,720
| |
Electric lamps | 0 | 2,750
| |
Paper mills | 2,500 | 0
|
For Additional Information:
EPA can provide further regulatory and other general information:
EPA Safe Drinking Water Hotline - 800/426-4791
Other sources of toxicological and environmental fate data include:
Toxic Substance Control Act Information Line - 202/554-1404
Toxics Release Inventory, National Library of Medicine - 301/496-6531
Agency for Toxic Substances and Disease Registry - 404/639-6000 National Pesticide Hotline
- 800/858-7378
List of Contaminants
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