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MERCURY, ELEMENTAL

Classification   |    Detailed evidence-based information

Therapeutic Toxic Class

    A) ELEMENTAL MERCURY
    1) Many forms of mercury exist. These major forms can be classified as elemental mercury, inorganic mercury (eg, inorganic mercury salts), and organic mercury. This document concerns elemental mercury only.
    a) Elemental mercury is not used as a therapeutic agent, but may occur in some medical instruments or in dental settings in which mercury vapor from dental amalgams may occur. Inhalation of elemental mercury vapor can result in toxicity. Acute toxicity is less likely to occur from other common routes of exposure unless the mercury is converted to an ionized form by acids or strong oxidants.
    b) Elemental mercury (vapor) is a RESPIRATORY TRACT, CNS, and RENAL HAZARD. Adverse effects involving the eyes, skin, gingiva, and other organs may occur.

Specific Substances

    1) Dental amalgam
    2) Hydrargyrum
    3) Kwik
    4) Liquid mercury
    5) Liquid silver
    6) Mercure
    7) Mercurio
    8) Mercury
    9) Mercury amalgam
    10) Mercury dust
    11) Mercury vapor
    12) Metallic mercury
    13) Quicksilver
    14) CAS 7439-97-6
    15) QUECKSILBER
    16) RTEC
    1.2.1) MOLECULAR FORMULA
    1) Hg

Available Forms Sources

    A) FORMS
    1) Elemental mercury is a silvery liquid that is heavy, mobile, non-wetting, slightly volatile and odorless (Bingham et al, 2001; Budavari, 2000; Lewis, 1998). In its solid state, mercury is a tin-white, ductile metal that is malleable enough to be cut with a knife (Budavari, 2000).
    2) Near its boiling point of 356.9 degrees Celsius, mercury is slowly oxidized to mercuric oxide in the presence of oxygen (Bingham et al, 2001; Budavari, 2000).
    3) Mercury is available in the following grades: commercial, instrument, redistilled, technical and triple distilled. Standard commercial grade contains 99.9 percent mercury ((HSDB, 2002)).
    B) SOURCES
    1) Alpha mercuric sulfide (i.e., red mercury, cinnabar, cinnabarite) is the primary ore from which mercury is extracted and processed (Harbison, 1998a; IARC, 1997). Mercury ore is also found in rocks of many varieties, including: limestone, calcareous shales, sandstone, serpentine, chert andesite, basalt and rhyolite ((HSDB, 2002)).
    2) Mercury exists naturally in the earth's crust at 0.5 ppm (Budavari, 2000).
    3) The primary source of atmospheric mercury is from degassing of mercury from soil and surface waters. Fossil fuel burning, the disposal of solid wastes which contain mercury, and the use of mercury containing fungicides, pesticides, paints and other products, also contribute to atmospheric mercury concentrations (Harbison, 1998a; US DHHS, 1992). It is also released into the atmosphere from volcanoes and hot springs (Harbison, 1998a; (HSDB, 2002)).
    4) SOURCES OF EXPOSURE
    a) MERCURY VAPOR - exposure can result from breaking of mercury fluorescent light bulbs (Yang et al, 1994; Tunnessen et al, 1987), heating of mercury-gold amalgams in order to extract gold (Kanluen & Gottlieb, 1991), and the use of mercury-containing latex paint (Agocs et al, 1990) or building materials and vacuuming of carpet contaminated with mercury ((ATSDR, 1999)). Ingestion or handling of liquid mercury following breakage of thermometers or other mercury-containing devices are other sources of exposure ((ATSDR, 1999)).
    b) Insertion or removal of dental amalgam restorations can generate mercury vapor or respirable particulates (Nimmo et al, 1990; Eley & Cox, 1993; Powell et al, 1994; US DHHS, 1992). Mercuric ions may also be produced during the life of a restoration (Eley & Cox, 1993) or with the use of whitening agents (Hummert et al, 1993). Bruxism, chewing (food or gum {in particular long-term use of nicotine chewing gum} and tooth brushing may increase amalgam release of mercury vapor (Goering et al, 1992; Clarkson et al, 2003).
    c) FLUORESCENT LIGHT BULBS - Fluorescent light bulbs contain a very small amount (4 to 6 mg) of mercury inside a glass tubing. In contrast, a thermometer contains about 500 mg of mercury. Health effects are not expected from acute exposure to a broken bulb.The EPA recommends the following clean-up and disposal guidelines if these bulbs are dropped or broken (US Environmental Protection Agency, 2007; US Environmental Protection Agency, 2007):
    1) HARD SURFACES - Open all windows and leave the room for at least 15 minutes. Use disposable rubber gloves and carefully collect the broken pieces and powder with stiff paper or cardboard. Then, use a wet paper towels or disposable wet wipes to clean the area. If needed, use sticky tape (eg; duct tape) to pick up small pieces and powder. Place everything collected in two sealed plastic bags in the outdoor trash container (in accordance with local household hazardous waste laws).
    2) CARPET OR RUGS - Follow the steps above. If vacuuming is required after all pieces were removed, vacuum the area and remove the vacuum bag (or empty the canister) and place the vacuum bag (or debris) in two sealed plastic bags in the outdoor trash.
    d) THERMOMETERS/INADVERTENT EXPOSURE - Elevated urine mercury levels have been seen in children of thermometer plant workers, presumably because of contamination of workers' clothing with elemental mercury which was then brought home (Hudson et al, 1987).
    e) THERMOSTATS: Elevated blood and urine concentrations (55 mcg/L and 15 mcg/mL, respectively) were reported in a man who injected himself with mercury obtained from a thermostat or thermometer (Tae et al, 2015).
    f) OCCUPATIONAL/DENTAL WORKERS - The use of silver amalgams can result in exposure to mercury vapor. Various studies over the past several decades have analyzed the potential health effects of long-term exposure. The potential risks of long-term low dose exposure continues to be debated in the literature. A recent concern is that long-term exposure to low concentrations of mercury vapor from amalgams can either cause or exacerbate degenerative diseases, such as amyotrophic lateral sclerosis, Alzheimer's disease, multiple sclerosis, and Parkinson's disease. At present, reviews of epidemiological evidence do not indicate an association (Bates, 2006; Clarkson et al, 2003). A more recent study of dental nurses exposed to silver amalgam 30 years previously found no differences in neurobehavioral test scores compared to controls. Overall, self-reported health status was similar between groups (Jones et al, 2007).
    1) The potential effects of dental amalgams have also been studied in pediatric populations. Bellinger et al (2007, 2006) prospectively studied children ages 6 to 10 years. After baseline assessment, children were randomized to receive either dental restoration with either amalgam or resin composite (mercury-free) material. At 5 years of follow up, children in the amalgam group had no difference in IQ scores or urinary albumin excretion (Bellinger et al, 2007; Bellinger et al, 2006). DeRouen (2006) et al reported similar findings at 7 years of follow up in a study of Portuguese children (DeRouen et al, 2006).
    g) BAROMETERS - Several children developed mercury poisoning after exposure to mercury containing devices (barometers that had been broken) found in school settings (Koyun et al, 2004).
    h) INTENTIONAL INGESTION of mercury occurs when it is used by some religious practitioners as a folk remedy for "empacho," a chronic stomach disorder or for other religious, ethnic or ritualistic practices ((ATSDR, 1999); Geffner & Sandler, 1980).
    i) MEDICAL EQUIPMENT/FEEDING TUBE - Peritoneal exposure to elemental mercury from the use of intestinal feeding tubes (rupture of the weighted portion has resulted in spillage of mercury into the peritoneal cavity) has occurred rarely (Haas et al, 2003).
    j) DOMESTIC EXPOSURE/INHALATION - In recent years, power companies in the US have attempted to replace pressure-control devices for domestic gas supply and inadvertent spills of liquid mercury have occurred in several incidences. Quicksilver (liquid metallic mercury), may still be found in homes in developing countries. It is used in cultural and religious ceremonies within the home (sprinkling mercury on floors or a car, burning it in candles or mixing it with perfume) (Hryhorczuk et al, 2006; Clarkson et al, 2003).
    k) MEDICAL PROCEDURE - Mercury emboli have occurred during some cardiac catheterization procedures (Gosselin et al, 1984).
    l) INHALATION of smoke from heated lime bricks which contained elemental mercury has also been reported (Mohan et al, 1994).
    m) An estimated 70,000 to 150,000 workers in the United States are exposed to mercury (various forms) on a regular basis. Occupations which have the greatest exposure to mercury vapors include mining and processing of cinnabar ore, the chlor-alkali industry, and occupations in which mercury-containing instruments or materials are manufactured or handled (Bingham et al, 2001; IARC, 1997).
    n) Dietary exposure to mercury (in the form of methyl mercury {organic mercury exposure}) occurs mainly from consumption of fish, shellfish and marine mammals ((ATSDR, 1999); IARC, 1997). Edible mushrooms may also contribute to dietary mercury exposure ((ATSDR, 1999)). See MERCURY, ORGANIC topic for further information.
    C) USES
    1) Elemental mercury is used in:
    1) Barometers, thermometers, thermostats, hydrometers, pyrometers, sphygmomanometers
    2) Boilers, propellant, Miller Abbott tubes
    3) Electrolytic production of chlorine and caustic soda (chlor-alkali industry)
    4) Fluorescent lamps, mercury arc lamps, switches, dry-cell batteries
    5) Gold mining, coolant, mirror coating, and as a neutron absorber in nuclear power plants
    6) Laboratory, agricultural and pharmaceutical chemicals (as an ingredient in many pharmaceuticals, diuretics, antiseptics)
    7) Manufacture of mercury cells and all mercury salts
    8) Pesticide and fungicide production
    2) REFERENCES: (Tae et al, 2015; (HSDB, 2002); (OHM/TADS, 2002); (ATSDR, 1999); Budavari, 2000; Harbison, 1998a; Lewis, 1998; IARC, 1997; ITI, 1995).
    3) BULLETS - Bullets which have been illegally hollowed out and filled with mercury have been used for animal control in some rural areas (Villalobos & Snodgrass, 1991).
    4) DENTAL AMALGAMS - The amalgam used in dental fillings contains approximately 50% metallic mercury ((ATSDR, 1999)). The World Health Organization estimated in 1991 that dental amalgams comprised 3 percent of the total use of mercury in industrialized countries (IARC, 1997).
    5) INSTRUMENTS OR DEVICES - Elemental mercury is also used in electrical apparatus, thermometers, sphygmomanometers, barometers, Miller Abbott tubes, and other instruments or devices (Hathaway et al, 1991; Lewis, 1998).
    6) PAINTS - Although mercury-containing interior latex paint has not been manufactured in the United States since 1990, and production of exterior mercury-containing paints was discontinued in 1991, these paints may still be available in some households. Mercury-containing paints, joint compounds, plasters, and adhesives manufactured in the US must have a warning label (US DHHS, 1992).
    7) FOLK MEDICINE - In some Mexican-American communities, elemental mercury is used as a folk medicine to treat "empacho," a chronic stomach disorder ((ATSDR, 1999); Geffner & Sandler, 1980).
    8) RELIGIOUS PRACTICES - Elemental mercury is sold under the name "azogue" for use in various religious, ethnic or ritualistic practices ((ATSDR, 1999)).

Life Support

    A) This overview assumes that basic life support measures have been instituted.

Clinical Effects

    0.2.1) SUMMARY OF EXPOSURE
    A) USES: Mercury exists in 3 forms: elemental, inorganic, and organic. Each causes distinct toxicity patterns. This document discusses ONLY ELEMENTAL mercury. Elemental mercury (quicksilver) is found in thermometers, barometers, sphygmomanometers, dental amalgams, fluorescent light bulbs, Mexican-American folk medicine, and in some medical equipment (eg, tip of Dobhoff tubes); it is also used in the gold mining industry. Severe toxicity is unusual, and most often develops from vaporization from heating mercury in a closed space. Moderate toxicity may develop from vaporization by vacuuming a mercury spill (ie, a broken thermometer), or prolonged inhalation exposure.
    B) TOXICOLOGY: Mercury covalently binds the sulfur moiety in sulfhydryl groups throughout the body disrupting enzymes, membranes, structural proteins, and transport mechanisms. Toxicity develops as elemental mercury is oxidized to the mercurous (Hg+) and mercuric (Hg2+) forms that interact with these entities causing multiorgan dysfunction.
    C) EPIDEMIOLOGY: Mercury thermometer exposures are not uncommon, but people rarely get sick. Other elemental mercury poisonings are uncommon, but deaths occur.
    D) WITH POISONING/EXPOSURE
    1) INGESTION: Ingestion is generally nontoxic in an intact gastrointestinal tract, but mucosal breaks and prolonged contact may increase absorption. Symptoms may resemble inorganic mercury poisoning.
    2) INHALATION: Adverse effects mainly result from vapor inhalation and primarily affect the lungs. Pulmonary pathology includes pneumonitis, necrotizing bronchiolitis, pulmonary edema, acute lung injury, and death. Central nervous system effects, renal damage, gingivitis, and stomatitis can also develop. Within a few hours of high concentration of mercury vapor exposure, weakness, chills, metallic taste, nausea, vomiting, diarrhea, abdominal pain, headache, tremor, visual disturbances, dyspnea, cough, and chest tightness may develop.
    3) INTRAVENOUS OR INTRAMUSCULAR: IV injection may rarely result in pulmonary embolism, and IM injection may lead to renal dysfunction and chronic absorption; signs and symptoms are usually mild, but may be similar to inorganic mercury toxicity.
    4) CHRONIC: Chronic mercury poisoning (mercurialism) usually results from inhalation of elemental mercury vapor or particles. Evidence of chronic poisoning may occur within weeks of an extreme acute exposure or may develop insidiously over many years. Chronic inhalation leads to the classic triad of neuropsychiatric disturbances (ie, personality changes, hallucinations, delirium, insomnia, irritability, fatigue, memory loss, erethism), tremor (fine intention tremor of fingers that progresses to choreiform movements of limbs), and gingivostomatitis. Children and some adults develop acrodynia associated with severe leg cramps, irritability, insomnia, diaphoresis, hypertension, miliarial rash, and peeling erythematous skin on the fingers, hands, and feet. Renal dysfunction has been reported.
    0.2.4) HEENT
    A) Stomatitis, swelling of the salivary glands and gingivitis may develop within a few days of acute exposure to mercury. Teeth may become loose due to gum inflammation.
    0.2.10) GENITOURINARY
    A) Mercury vapor exposure may result in proteinuria or nephrotic syndrome. Acute tubular necrosis and renal failure may develop. Dysuria and ejaculatory pain have been reported following acute exposure. Transient abnormalities in urinary electrolytes may occur.
    0.2.21) CARCINOGENICITY
    A) Metallic mercury and inorganic mercury compounds are listed as Group 3 (not classifiable as to their carcinogenicity in humans) by the IARC CANCER REVIEW, based on inadequate evidence in humans for the carcinogenicity of mercury and mercury compounds, inadequate evidence in experimental animals for the carcinogenicity of metallic mercury, and limited evidence in experimental animals for the carcinogenicity of mercuric chloride (IARC, 1997).

Laboratory Monitoring

    A) 24-hour urinary mercury concentration is the best marker for chronic exposure (patient should abstain from eating seafood for a week or the placement of mercury amalgams for several weeks prior to collection). Whole blood mercury concentration may be useful for acute exposure. Careful specimen collection is important to avoid contamination. A laboratory should use trace element collection tubes for blood samples and acid-washed containers for a 24-hour urine collection. Mercury levels of 10 mcg/L for whole blood and 20 mcg/L for urine typically reflect background exposure.
    B) Monitor serum electrolytes, renal function, glucose, urinalysis and liver enzymes in symptomatic patients.
    C) Monitor chest radiograph in patients with pulmonary symptoms.
    D) Specific urine markers for renal injury should include beta-2 microglobulin, microalbuminuria, and retinol binding protein in symptomatic patients.
    E) Postchelation mercury concentrations should not be utilized as the sole basis for the diagnosis of mercury poisoning and subsequent treatment. This is especially true if no baseline, prechelation concentration was measured.

Treatment Overview

    0.4.2) ORAL/PARENTERAL EXPOSURE
    A) MANAGEMENT OF TOXICITY
    1) INGESTION: Ingestion usually does not result in acute toxicity since elemental mercury is poorly absorbed. Obtain an x-ray to document its presence and course. Whole bowel irrigation may assist in cases of large volume ingestion, prolonged retention, mucosal inflammation, or fistula. Surgical removal is almost never needed. Postural drainage or suctioning may aid in the removal of aspirated elemental mercury.
    2) INHALATION: Inhalation is the prime source of significant toxicity, especially after vaporization from heating or vacuuming spills. Ventilate the area for 15 minutes and pick up mercury globules with cardboard or duct tape. If vacuuming is required, discard the bag in 2 sealed plastic bags immediately after use. Thermometers contain about 500 mg of mercury and can cause significant injury if vaporized by vacuuming. Move the patient to fresh air. Monitor for respiratory distress and hypoxia. Give 100% humidified oxygen, intubate, and assist ventilation as needed. Administer beta-2 adrenergic agonists for bronchospasm. Severe pulmonary toxicity may mandate admission to an intensive care unit for meticulous supportive care and respiratory management.
    3) INTRAVENOUS or INTRAMUSCULAR: IV or IM injection usually requires only supportive care.
    B) DECONTAMINATION
    1) PREHOSPITAL: Irrigate the eyes and ski, if exposed. Remove contaminated clothing. Move the patient to fresh air. No charcoal is needed.
    2) HOSPITAL: Whole bowel irrigation may assist in cases of large volume ingestion, prolonged retention, mucosal inflammation, or fistula. Surgical removal is almost never needed.
    C) AIRWAY MANAGEMENT
    1) Manage the airway as needed. Inhalational exposure is the main determinant of pulmonary disease.
    D) ANTIDOTE
    1) Chelation has been used to facilitate elemental mercury removal, but clear data showing improved clinical outcomes are lacking. Chelation should be performed in patients with severe symptoms after acute exposure, and should be considered in patients who are symptomatic after chronic exposure. Asymptomatic patients with elevated urinary mercury concentrations probably do not warrant chelation. Mercury chelators include primarily succimer (given orally and most often used for chronic poisoning), dimercaprol (administered IM, used in patients with severe acute poisoning), and unithiol (used in Europe and available from compounding pharmacies in the United States, can be given IV for severe acute poisoning or orally for less severe or chronic poisoining), but D-penicillamine, and N-acetyl penicillamine have also been used.
    2) Parenteral chelation (intramuscular Dimercaprol (BAL) or intravenous unithiol) therapy should be initiated in patients with significant acute exposures (acute inhalation with pulmonary, GI or neurologic effects). BAL is given in decreasing doses over 10 days if the patient is unable to take oral medications. The dosing schedule is as follows: 5 mg/kg initially, followed by 2.5 mg/kg 1 or 2 times daily for 10 days. When the patient is improving and able to tolerate oral medications, BAL can be replaced with succimer with no waiting period between treatments. Succimer may given based on the following dosing schedule: 1) 10 mg/kg orally 3 times daily for 5 days then 2) 10 mg/kg 2 times daily for 14 days. Succimer may be used alone in chronically exposed patients. Unithiol (2,3-dimercaptopropanol-sulfonic acid, DMPS) is available through compounding pharmacies in the United States. It is a water-soluble analog of BAL, and can be given orally or parenterally. It is considered a better mercury chelator than succimer. Unithiol is dosed as follows: IV: Day one 250 mg/kg every 3 to 4 hours, day two 250 mg every 4 to 6 hours, day three 250 mg every 6 to 8 hours, day four 250 mg every 8 to 12 hours, days five and six: 250 mg every 8 to 24 hours. Depending on the patient's clinical status, therapy may be changed to the oral route after the fifth day: 100 to 300 mg 3 times daily. ORAL: Initially 1200 mg to 2400 mg every 24 hours divided (100 mg or 200 mg every 2 hours), reduce to 100 mg to 300 mg every 8 hours as tolerated. Patients should be treated for 14 days or until there is no mercury detected in the urine.
    E) ENHANCED ELIMINATION
    1) There is no role for hemodialysis or hemoperfusion.
    F) PATIENT DISPOSITION
    1) HOME CRITERIA: Asymptomatic patients with brief, , low-dose vapor exposures, tract may be observed at home. Patients with unintentional ingestion of less than the amount of mercury in a fever thermometer who do not have abdominal pain can be observed at home. They may be referred to their physician at a convenient time for an x-ray to document the mercury's course after ingestion. If a small mercury spill has been vacuumed or swept the health department should be notified to perform environmental monitoring and the patient referred for evaluation if ambient concentrations are high.
    2) OBSERVATION CRITERIA: The following patients should be referred to a healthcare facility for observation and treatment: patients with suspected self-harm, abuse, or malicious use of elemental mercury; patients with symptoms of acute (eg, cough, dyspnea, chest pain) or chronic (eg, rash, tremor, weight loss) exposure to elemental mercury; exposure to recently heated (eg, stove top, oven, furnace) elemental mercury; patients exposed to documented high air mercury concentrations; patients who ingested more mercury than in a household fever thermometer or those with abdominal pain after ingestion; patients with elemental mercury deposited or injected into soft tissue. Observe patients with inhalation exposure for 6 to 12 hours for respiratory disease progression. The results of blood and urine mercury concentrations (usually require an outside laboratory analysis) will not influence acute care.
    3) ADMISSION CRITERIA: Any symptomatic patient (dyspnea, hypoxia, wheezes, gastrointestinal complaints) should be admitted to the intensive care unit. Patients with chronic exposure should be removed from exposure and chelated if symptomatic; this may require admission.
    4) CONSULT CRITERIA: Consult a toxicologist for assistance in managing patients with mercury toxicity.
    G) PITFALLS
    1) Misidentification of the type of mercury exposure (elemental, inorganic, organic). Recent seafood consumption will elevate urinary mercury concentration.
    H) TOXICOKINETICS
    1) Absorption is negligible (0.1%) in a normal gastrointestinal tract, but increases with mucosal breaks and with prolonged contact due to increased chances for oxidation to more readily absorbed inorganic forms. It is well absorbed via inhalation. It distributes to the kidneys and CNS, and is cleared by renal and gastrointestinal routes with an elimination half-life of about 30 to 60 days.
    I) PREDISPOSING CONDITIONS
    1) Occupational exposure, hobbies involving gold extraction, and folk medicine may predispose to toxicity.
    J) DIFFERENTIAL DIAGNOSIS
    1) Pheochromocytoma; Kawasaki's disease; brucellosis; Creutzfeldt-Jakob disease.
    0.4.3) INHALATION EXPOSURE
    A) INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm.
    0.4.4) EYE EXPOSURE
    A) Elemental mercury droplets may be absorbed after conjunctival contact. Irrigate with room-temperature water for at least 15 minutes and consider ophthalmic examination if local effects persist.
    0.4.5) DERMAL EXPOSURE
    A) OVERVIEW
    1) Allergic contact dermatitis may result from repeated or prolonged skin contact. Skin absorption of elemental mercury is limited.

Range Of Toxicity

    A) TOXICITY: Exposure to broken fluorescent light bulbs containing mercury (4 to 6 mg) is not expected to produce toxicity. Thermometers contain about 500 mg of elemental mercury and can cause symptomatic poisoning if vaporized by vacuuming. Young children have developed toxicity after less than 2 weeks of exposure to mercury generated by a glass thermometer that broke and spilled on carpet, and after the spillage of 0.5 to 1 ounce of mercury in a home. The amount of ingested mercury that would be fatal to a man is estimated at 100 grams (1429 mg/kg). A man ingested 500 g (66 mL) of elemental mercury (quicksilver) in a suicide attempt, but survived following supportive care.

Summary Of Exposure

    A) USES: Mercury exists in 3 forms: elemental, inorganic, and organic. Each causes distinct toxicity patterns. This document discusses ONLY ELEMENTAL mercury. Elemental mercury (quicksilver) is found in thermometers, barometers, sphygmomanometers, dental amalgams, fluorescent light bulbs, Mexican-American folk medicine, and in some medical equipment (eg, tip of Dobhoff tubes); it is also used in the gold mining industry. Severe toxicity is unusual, and most often develops from vaporization from heating mercury in a closed space. Moderate toxicity may develop from vaporization by vacuuming a mercury spill (ie, a broken thermometer), or prolonged inhalation exposure.
    B) TOXICOLOGY: Mercury covalently binds the sulfur moiety in sulfhydryl groups throughout the body disrupting enzymes, membranes, structural proteins, and transport mechanisms. Toxicity develops as elemental mercury is oxidized to the mercurous (Hg+) and mercuric (Hg2+) forms that interact with these entities causing multiorgan dysfunction.
    C) EPIDEMIOLOGY: Mercury thermometer exposures are not uncommon, but people rarely get sick. Other elemental mercury poisonings are uncommon, but deaths occur.
    D) WITH POISONING/EXPOSURE
    1) INGESTION: Ingestion is generally nontoxic in an intact gastrointestinal tract, but mucosal breaks and prolonged contact may increase absorption. Symptoms may resemble inorganic mercury poisoning.
    2) INHALATION: Adverse effects mainly result from vapor inhalation and primarily affect the lungs. Pulmonary pathology includes pneumonitis, necrotizing bronchiolitis, pulmonary edema, acute lung injury, and death. Central nervous system effects, renal damage, gingivitis, and stomatitis can also develop. Within a few hours of high concentration of mercury vapor exposure, weakness, chills, metallic taste, nausea, vomiting, diarrhea, abdominal pain, headache, tremor, visual disturbances, dyspnea, cough, and chest tightness may develop.
    3) INTRAVENOUS OR INTRAMUSCULAR: IV injection may rarely result in pulmonary embolism, and IM injection may lead to renal dysfunction and chronic absorption; signs and symptoms are usually mild, but may be similar to inorganic mercury toxicity.
    4) CHRONIC: Chronic mercury poisoning (mercurialism) usually results from inhalation of elemental mercury vapor or particles. Evidence of chronic poisoning may occur within weeks of an extreme acute exposure or may develop insidiously over many years. Chronic inhalation leads to the classic triad of neuropsychiatric disturbances (ie, personality changes, hallucinations, delirium, insomnia, irritability, fatigue, memory loss, erethism), tremor (fine intention tremor of fingers that progresses to choreiform movements of limbs), and gingivostomatitis. Children and some adults develop acrodynia associated with severe leg cramps, irritability, insomnia, diaphoresis, hypertension, miliarial rash, and peeling erythematous skin on the fingers, hands, and feet. Renal dysfunction has been reported.

Vital Signs

    3.3.3) TEMPERATURE
    A) FEVERS are often reported in both children and adults following elemental mercury exposure (Tezer et al, 2012; Truche et al, 2012; Sevketoglu et al, 2011; Wale et al, 2010; McFee & Caraccio, 2001; Bluhm et al, 1992a; Snodgrass et al, 1981; Florentine & Sanfilippo, 1991; Moutinho et al, 1981; Mohan et al, 1994), and may be misinterpreted as infectious illness or metal fume fever (Truche et al, 2012; Sevketoglu et al, 2011; Wale et al, 2010; McFee & Caraccio, 2001; Bluhm et al, 1992a; Snodgrass et al, 1981; Florentine & Sanfilippo, 1991; Moutinho et al, 1981; Mohan et al, 1994).

Heent

    3.4.1) SUMMARY
    A) Stomatitis, swelling of the salivary glands and gingivitis may develop within a few days of acute exposure to mercury. Teeth may become loose due to gum inflammation.
    3.4.2) HEAD
    A) WITH POISONING/EXPOSURE
    1) CHRONIC EXPOSURE: Discoloration of the lens, corneal opacity, band keratopathy, and impaired vision may occur with chronic exposure. Nasal irritation, epistaxis, gingivitis, stomatitis, tremor of the tongue, and disturbed sense of taste and smell may develop. Speech defects may occur in severe cases of chronic mercury exposure (Gosselin et al, 1984; Yang et al, 1994).
    3.4.3) EYES
    A) WITH POISONING/EXPOSURE
    1) MERCURY DEPOSITION
    a) External eye contact with liquid mercury has resulted in temporary mercury deposition beneath the corneal epithelium, without apparent adverse effects.
    2) CONJUNCTIVITIS
    a) Vapors may cause conjunctivitis.
    3) EYELID TREMORS
    a) Eyelid tremors may occur following acute or chronic mercury exposure.
    4) MERCURIALENTIS
    a) Eye exposure to mercury vapors, or systemic mercury poisoning may result in mercurialentis, a brownish discoloration of the lens. Mercurialentis usually indicates chronic exposure to elemental mercury rather than toxicity. Diagnosis is made by slit lamp examination (Rosenmann et al, 1986; Winship, 1985).
    5) PAPILLEDEMA
    a) CASE REPORT: A 12-year-old boy who was chronically exposed to elemental mercury at home, presented with a 1-month history of severe fatigue, generalized muscle pain, and weakness. On presentation, he had painful extremities, decreased motor strength, and lack of deep tendon reflexes in lower extremities. An electromyography revealed mixed type polyneuropathy. Laboratory results showed elevated whole blood and 24-hour urinary mercury concentrations (23.2 mcg/L [normal: 0 to 10 mcg/L] and 175 mcg/L [normal: 0 to 15 mcg/L], respectively). Despite treatment with succimer which was started on day 4, he developed headache, nausea, bilateral papilledema, and intracranial hypertension 7 days after presentation. Following further supportive care, including treatment with acetazolamide, his condition gradually improved and he was discharged after 35 days of hospitalization with acetazolamide, vitamin B6, and gabapentin (Gencpinar et al, 2015).
    6) EFFECTS OF LONG TERM EXPOSURE
    a) Mercurialentis, band keratopathy, corneal opacity, and impaired vision are primarily associated with chronic mercury exposure (Grant, 1986). A study cited by Sue (1994) reported constriction of the visual fields after 2 weeks of mercury vapor exposure (Sue, 1994).
    b) A 10-year-old boy developed transient blurred vision and diplopia after exposure to elemental mercury for 20 days (Abbaslou & Zaman, 2006).
    7) EFFECTS OF INJECTED MERCURY
    a) BLINDNESS: Injection of mercury into the arterial circulation during cardiac catheterization has caused retinal artery embolism and blindness. Injection of mercury into the eye has caused severe eye injury in animals (Grant, 1986).
    8) CHRONIC EXPOSURE
    a) A study cited by Sue (1994) reported constriction of the visual fields after 2 weeks of mercury vapor exposure (Sue, 1994). Chronic exposure to mercury by any route may result in mercurialentis, a brownish discoloration of the lens of the eye. Corneal opacities, band keratopathy, and impaired vision (Grant, 1986) as well as photophobia (Karagol et al, 1998) have been reported.
    b) Mercurialentis usually indicates chronic exposure to elemental mercury rather than toxicity. Diagnosis is made by slit lamp examination (Winship, 1985; Rosenmann et al, 1986).
    9) COLOR VISION DISTURBANCE
    a) Workers exposed to elemental mercury had subclinical color vision loss, mainly in the blue-yellow range compared with controls. Workers with urinary mercury concentration greater than 50 micrograms/gram creatinine were more likely to be affected (Cavalleri et al, 1995).
    b) In a follow-up study, subclinical color discrimination impairment was observed in workers exposed to mercury at an exposure level (a limit of 35 mcg/g creatinine based on renal effects has been proposed) below the current biological limit for occupational exposure to mercury (Urban et al, 2003).
    c) Another study reported that color discrimination impairment (mainly blue-yellow and red-green) can be found years (6.8 +/- 4.2 years; range 1 to 15 years) after cessation of mercury vapor exposure and may be irreversible (Feitosa-Santana et al, 2008).
    10) INTRAOCULAR MERCURY INJECTION
    a) CASE REPORT: A 27-year-old woman, with a history of schizophrenia, developed photophobia and painless visual loss after intraocular injection with metallic mercury. Examination revealed severely diminished visual acuity (20/800 OD and light perception OS), bilateral subconjunctival hemorrhage, panuveitis, hypopyon, vitiritis and peripheral retinal necrosis. This progressed to nearly complete visual loss and bilateral retinal detachment. CT and plain radiographs revealed intraorbital and intraocular metallic foreign bodies and mercury concentration in the vitreous and urine was elevated. Bilateral exenteration was performed to remove all mercury in the eyes. Approximately one quarter of the volume of each eyeball was filled with metallic mercury (Auer et al, 1997).
    3.4.6) THROAT
    A) Respiratory tract irritation, coughing, a metallic taste, and swelling of the salivary glands may occur with acute exposure to vapors. Gingivitis and stomatitis are commonly described following acute elemental mercury exposure (Setz et al, 2008; Snodgrass et al, 1981; Bluhm et al, 1992a).
    1) Dark spots or dark bluish lines along the gums may develop (Gosselin et al, 1984; Yang et al, 1994).
    2) CASE REPORT: A 15-month-old girl with severe mercury poisoning developed gingivitis and premature exfoliation of her primary teeth associated with necrotic mandibular bone (Martin et al, 1997).
    3) Oral hypersensitivity to mercury in amalgams may mimic lichen planus (Camisa et al, 1999; Laine et al, 1999).
    B) Teeth may become loose due to gum inflammation. However, poor dental health is not always associated with chronic exposure to mercury vapor as observed among chloralkali workers (Holland et al, 1994).
    C) CASE REPORT: Extensive gingival ulceration and loss of 6 teeth were observed in an 11-year-old girl who presented with a 7-week history of back pain, anorexia, weight loss, fatigue and behavioral disturbances (periodic confusion, aggression, confabulations, and secondary encopresis) following exposure to mercury from a broken industrial thermostatic clock. Physical examination also revealed acrodynia, tremor, cachexia, and hypertension. Following chelation therapy with DMPS for 9 weeks, she recovered gradually (van der Linde et al, 2009).

Cardiovascular

    3.5.2) CLINICAL EFFECTS
    A) HYPOTENSIVE EPISODE
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 35-year-old woman who had been inhaling a mixture of burning dried lime filled with elemental mercury, mercuric oxide powder, and dried leaves as a folk remedy presented with a blood pressure of 70/50 mmHg (Mohan et al, 1994).
    B) HYPERTENSIVE EPISODE
    1) WITH POISONING/EXPOSURE
    a) Hypertension and tachycardia have been reported in children with intoxication from exposure to elemental mercury (eg, playing with metallic mercury found in barometers or sphygmomanometers that had broken) (Mercer et al, 2012; Setz et al, 2008; Celebi et al, 2008; van der Linde et al, 2009; Abbaslou & Zaman, 2006; Kosan et al, 2001; Velzeboer et al, 1997; Wobmann et al, 1999; Rennie et al, 1999; Martin et al, 1997; Koyun et al, 2004). Hypertension has also been reported in adults (Cicek-Senturk et al, 2014). Mercury-induced hypertension increases levels of epinephrine and norepinephrine due to inhibition of catechol-O-methyltransferase; therefore, first-line antihypertensive agents may not be effective (Koyun et al, 2004).
    C) TACHYCARDIA
    1) WITH POISONING/EXPOSURE
    a) Tachycardia and hypertension have been reported in children with intoxication from exposure to elemental mercury (eg, playing with metallic mercury found in barometers or sphygmomanometers that had broken) (van der Linde et al, 2009; Celebi et al, 2008; DePalma et al, 2008; Abbaslou & Zaman, 2006; Kosan et al, 2001; Velzeboer et al, 1997; Wobmann et al, 1999; Rennie et al, 1999; Martin et al, 1997; Koyun et al, 2004). Tachycardia has also been reported in adults (Cicek-Senturk et al, 2014).
    D) EMBOLUS
    1) Mercury embolization to the lungs and heart and cardiac granulomas were reported at autopsy in a 24-year-old man who had intravenously injected elemental mercury 5 months prior to his death from narcotic overdose (Kedziora & Duflou, 1995).
    2) Mercury emboli were detectable (via CT scan) in the right ventricle and coronary artery of a 27-year-old man following intravenous injection of 1.5 mL elemental mercury. The right ventricular deposits were still present on repeat CT 66 days later (Eyer et al, 2006).
    3) CASE REPORT: A 40-year-old man developed dyspnea, fever, tachycardia, and mild gastrointestinal disturbances after the intravenous injection of 3 mL of elemental mercury and ingestion of 3 mL in a suicide attempt. Chest X-ray showed scattered pulmonary infiltrates and embolized mercury bilaterally. In addition, he had minor elevations in BUN and serum creatinine and decreased urine output. Following chelation therapy, his pulmonary and renal functions improved over the next 36 hours (McFee & Caraccio, 2001).
    E) CHEST DISCOMFORT
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 22-year-old woman presented with a 2-hour history of chest discomfort after injecting herself on the forearm intravenously an unknown amount of elemental mercury from 3 thermometers mixed with alcohol in a suicide attempt. Radiopaque deposits of mercury, mainly in the middle and lower lobes of bilateral lung fields and in the pericardium, intenstine, kidneys, and liver were observed in a radiography. Despite normal vital signs on presentation, her mental status deteriorated with confusion, disorientation, tremor, and finally stupor (GCS score of 9) 2 to 3 hours after presentation. She also developed seizures and was treated with diazepam, and valproate acid after she developed epileptic crisis. Following supportive care, including treatment with a dimercaptosuccinic acid (DMSA)/succimer (800 mg orally 3 times daily for 5 days and 600 mg orally 3 times daily for 14 days) and phenytoin (125 mg IV 3 times daily), her mental status improved 2 hours later. CT scans of thorax, abdomen, and brain revealed multiple radiopaque nodes in both lungs, small pleural effusion, a few mercury deposits on the pericardium, multiple deposits on the liver, left kidney, spleen and paraspinal muscles. She was discharged 20 days after presentation, but experienced several seizures during the next 6 months. On a 2-year followup, she was stable without additional seizures (Karatapanis et al, 2015).

Respiratory

    3.6.2) CLINICAL EFFECTS
    A) PNEUMONITIS
    1) Hemoptysis, cyanosis, cough, chest tightness, pneumonitis, necrotizing bronchiolitis and pulmonary edema have occurred following vapor inhalation (Zimmerman, 1969; Tsuji et al, 1970; Tennant et al, 1961; Kanluen & Gottlieb, 1991; US DHHS, 1992; Mohan et al, 1994; Anon, 2005).
    2) Children less than 30 months of age may be at increased risk of adverse pulmonary effects following vapor exposure (US DHHS, 1992).
    3) CASE REPORT: A 62-year-old man developed cough, dyspnea, and lethargy after attempting to extract gold from an amalgam containing mercury by heating the amalgam in an aluminum pan. He was exposed for 3 hours via fumes and through direct skin contact. A chest x-ray revealed extensive alveolar shadowing indicating pneumonitis. Laboratory findings revealed blood mercury concentration of 5933 nmol/L (level of concern: greater than 70 nmol/L), an elevated white cell count (16.3 x 10(9)/L, reference interval [RI]: 4 to 11 x 10(9)/L), a platelet count of 617 x 10(9) (RI 150 to 400 x 10(9)/L), an abnormal serum albumin concentration (21 g/L, RI: 34 to 48 g/L), and mildly elevated liver enzymes. A urinalysis revealed a mercury concentration of 7556 nmol/L and the mercury:creatinine ratio of 2519 nmol/mmol (level of concern: greater than 5.8 nmol/mmol). Following supportive care, including treatment with dimercaptosuccinic acid (DMSA) (800 mg 3 times daily for 7 days followed by a dose reduction to 800 mg twice daily for an additional 14 days) and prednisolone (50 mg daily with a gradual dose taper down to zero over 3 weeks), his symptoms gradually resolved. A 3-week re-assessment showed ongoing elevated blood mercury concentrations (blood mercury 418 nmol/L), therefore he was re-challenged with DMSA 800 mg 3 times daily for 34 days (starting 66 days after exposure). Despite the improvement of symptoms following prolonged course of DMSA, he re-presented with fatigue, increasing peripheral edema, nausea, and vomiting. Biochemical analysis revealed severe nephrotic syndrome and he was subsequently treated with prednisolone, regular infusions of concentrated albumin, diuretics, and was restricted to 1.2 L of fluids daily. His condition gradually normalized over the next 4 months (Saleem et al, 2013).
    B) ACUTE LUNG INJURY
    1) Acute lung injury may occur following an acute inhalation of fumes from heated elemental mercury. Patients may present with fever, cough, dyspnea, chest pain, erythematous rash, itching, chills, gastrointestinal complaints, metallic taste, headache, and weakness (Cicek-Senturk et al, 2014).
    a) CASE REPORT: A 52-year-old woman presented with a 15-day history of high fever (39 degrees C on presentation), sore throat, itchy rash, generalized muscle pain, and nausea. Her husband and son had similar symptoms. Despite treatment with penicillin G, antihistaminic and antipyretic agents, and depot steroid treatments, her condition did not improve. Physical examination revealed a generalized maculopapular rash over her entire body, and bilateral cervical and axillary painful and mobile lymphadenopathies. Laboratory results revealed elevated serum urea, serum creatinine, lactate dehydrogenase, total protein, albumin, WBC, and C-reactive protein and decreased hemoglobin. Hepatomegaly was observed in an abdominal ultrasonography. A chest radiography showed several uncertain modular lesions. After several days of symptomatic treatment while trying to exclude malignancies and infectious and autoimmune diseases, it was revealed that the patient's son had brought mercury home from school. The family was exposed to mercury fumes after he spilled the mercury on the hot stove. About 10 hours later, her husband developed dyspnea, hypertension, tachycardia, high fever, and sore throat. Laboratory results revealed leucocytosis. Following supportive care, his symptoms improved and he was discharged after 8 days of hospitalization, but he developed a personality disorder several days later. Her son developed high fever, sore throat, skin rash, diarrhea, dyspnea, a generalized maculopapular rash, hyperemia in the conjunctivas, cervical bilateral axillary lymphadenopathy, and leukocytosis after exposure to mercury fumes. All patients were treated with penicillamine 300 mg every 6 hours for 7 days (Cicek-Senturk et al, 2014).
    2) CASE REPORT: One study reported bilateral pneumothoraces, and pulmonary findings similar to those of ARDS, in a 3-month-old following inhalation of mercury vapors. The infant's grandfather had been heating mercury over the kitchen stove in order to extract gold from gold ore. The infant developed tachypnea and irritability 4 hours after the gold extraction process (Moromisato et al, 1994).
    3) ARDS and fatal respiratory failure developed in 4 adults exposed to heated mercury vapor after trying to extract silver from dental amalgam in their home (Rowens et al, 1991; Taueg et al, 1992).
    4) CASE SERIES: A family, including 2 adults (ages of 38 years and 58 years) and 6 children (ranging in ages of 45 days to 14 years), developed respiratory symptoms, becoming subsequently fatal in two cases, after inhaling mercury vapors resulting from home gold ore processing. The spot urine mercury levels in the 8 family members ranged from 27 mcg/L to 682 mcg/L. The blood mercury levels in 4 of the 8 family members ranged from 117 mcg/L to 322 mcg/L (Solis et al, 2000).
    a) A 13-month-old child presented to the hospital with hypoxemia. Initial chest x-rays showed bronchial thickening. Within 24 hours, his respiratory status worsened, necessitating mechanical ventilation. Despite receiving surfactant and nitric oxide in order to improve his lung mechanics, he developed acute respiratory distress syndrome (ARDS) and multiple pneumothoraces. On the 25th day of hospitalization, he experienced cardiopulmonary arrest and died. Postmortem analysis of his lungs indicated chemical pneumonitis (Solis et al, 2000).
    b) The 38-year-old mother presented to the hospital with a non-productive cough and severe respiratory distress 48 hours post-exposure. A chest x-ray revealed diffuse bilateral alveolar infiltrates. Despite chelation therapy with DMSA and administration of corticosteroids, the patient developed ARDS, sepsis, and multiorgan failure, subsequently resulting in death. Postmortem analysis of her lungs indicated congestion and thickening of the alveolar septa with denudation of the epithelial lining (Solis et al, 2000).
    5) CASE REPORT: A 2.5-year-old boy developed lethargy and respiratory distress after exposure to mercury vapor. On presentation, he had mild dyspnea, tachypnea (a respiratory rate of 45/min) and an oxygen saturation of 88%. Blood gas analysis showed mild respiratory acidosis. His blood mercury level was 512 mcg/L and random urine mercury level was 165 mcg/L. A chest x-ray showed bilateral paracardiac infiltration with hyperinflation. Following supportive care, including treatment with D-penicillamine, NAC, and multivitamins, he recovered gradually (Sevketoglu et al, 2011).
    6) CASE REPORT: A 14-year-old boy presented with a 2-week history of fever, body rash, nausea, and vomiting. His vital signs included a body temperature of 39 degrees C, heart rate of 104 beats/min, respiratory rate of 30 breaths/min, and a blood pressure of 110/55 mmHg. Physical examination revealed a widespread maculopapular rash on his trunk and all limbs, pink and swollen palms and soles, desquamation of his fingertips, and bilateral nonpurulent conjunctivitis. He was admitted for concerns of respiratory failure and received ceftriaxone and clarithromycin; however, his condition deteriorated over the next 5 days. At this time, his mother was also hospitalized with similar symptoms. Laboratory results revealed a blood mercury concentration of 311 mcg/L (reference range, 0.1 to 20 mcg/L) and a 24-hour urine mercury concentration of 130 mcg/L (reference range, 0.6 to 59 mcg/L). At this time, he admitted to bringing mercury from school chemistry laboratory to his home. Initially, he was treated with d-penicillamine (30 mg/kg/day), but his blood and urine mercury concentrations remained high. Following treatment with dimercaptosuccinic acid (DMSA), his blood and urine mercury concentrations normalized and his symptoms resolved (Tezer et al, 2012).
    C) PULMONARY ASPIRATION
    1) Aspiration of elemental mercury may result in hemoptysis, cyanosis, pneumonitis and respiratory distress.
    2) Chronic respiratory disease may occur as a result of mercury aspiration. Radiographs may show mercury droplets at the lung bases (Janus & Klein, 1982).
    D) PULMONARY EMBOLISM
    1) INTRAVENOUS INJECTION: Pulmonary embolization from intravenous injection of mercury has resulted in dyspnea, hemoptysis and metallic densities on chest radiograph and CT (Oliver et al, 1987; Maniatis et al, 1997). Pulmonary emboli have been reported to persist 21 to 66 days following IV injection (Eyer et al, 2006; McFee & Caraccio, 2001).
    a) CASE REPORT: A 30-year-old woman presented with mercury toxicity after self-injection and ingestion of approximately 500 g of mercury from 37 broken fever thermometers. Despite supportive treatment, she developed lung embolization complicated by acute respiratory distress syndrome (ARDS), toxic dermatitis, anemia, and mild hepato-renal impairment, and died 30 days after presentation (DePalma et al, 2008).
    2) CASE REPORT: A 20-year-old man presented with chest pain, fever, and hemoptysis 3 months after injecting approximately 5 mL of elemental mercury subcutaneously into his left forearm and 7 days after injecting 8 to 10 mL of elemental mercury intravenously. Multiple tiny metallic densities in the soft tissues at the site of the subQ injection were observed in the plain radiography of the left forearm. A chest radiograph showed multiple tiny, discrete, metallic densities throughout the lung parenchyma bilaterally, predominantly at the lung bases, as well as at both pulmonary hila and at both cardiophrenic angles. He was treated with penicillamine for a few months. Six weeks after presentation, a chest radiograph revealed some diminution in the quantity of mercury deposits in the lungs (Wale et al, 2010).
    E) FIBROSIS OF LUNG
    1) Severe, acute exposures may result in residual restrictive pulmonary disease and fibrosis (Sue, 1994).
    F) PULMONARY FUNCTION STUDIES ABNORMAL
    1) Intravenous injection of mercury with microemboli was associated with normal ventilatory function but decreased diffusing capacity of carbon monoxide and arterial oxygen tension in one patient (dell'Omo et al, 1996).
    2) INHALATION: Permanent impairment of pulmonary function may occur following elemental mercury inhalation despite chelation therapy (Lilis et al, 1985; Levin et al, 1988).
    3) CASE REPORT: A 40-year-old man developed dyspnea and tachypnea 24 hours after IV injection of approximately 40 g (3 mL) elemental mercury and the ingestion of 3 mL of mercury in a suicide attempt. The patient was hypoxic (pO2 60.9 mm Hg) and pulmonary function testing was consistent with a restrictive lung disease pattern (McFee & Caraccio, 2001).
    4) CASE REPORT: A 23-year-old woman presented with dyspnea after injecting herself with 5 mL of elemental mercury. All pulmonary function tests were normal. Following treatment with D-penicillamine for 12 days, she was discharged. She developed disabling generalized myoclonus of cortical origin and gait ataxia 2 years after the initial exposure. At this time, her serum mercury was 6 mcg/dL (normal, 0.06 to 5.9 mcg/dL) and urinary mercury levels were markedly high (80.0 mcg/L; normal, less than 20 mcg/L). The pulmonary function tests showed a restrictive lung disease. Her symptoms progressed over the next 2 years. A chest radiograph 4 years after the initial exposure revealed multiple radiopaque specks in the lungs and a chest CT revealed that elemental mercury was finely deposited along the pulmonary vessels. Her symptoms improved after the mercury deposits were cleared surgically from the injection site (Ragothaman et al, 2007).
    G) PULMONARY ASPIRATION
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 49-year-old ingested 200 mL (2709 g) of elemental mercury and aspirated during gastric lavage. Multiple mercury droplets were detectable on chest x-ray but no significant respiratory symptoms were reported. Whole blood mercury level peaked at 457 mcg/L 8 days later (Lech & Goszcz, 2006).

Neurologic

    3.7.2) CLINICAL EFFECTS
    A) ALTERED MENTAL STATUS
    1) Confused mental status has been reported following acute mercury vapor exposure. Neurological signs and symptoms are chiefly associated with chronic exposure (Mohan et al, 1994).
    2) Effects include personality changes, tremors (Schaumburg et al, 2009; Celebi et al, 2008; van der Linde et al, 2009; Chapman et al, 1990), headache, short term memory loss, poor appetite, shyness, insomnia, emotional lability, paresthesias, weakness (Gencpinar et al, 2015; Abbaslou & Zaman, 2006; Yeates & Mortensen, 1994; Lu et al, 1998) and nerve conduction delays (Rosenmann et al, 1986; US DHHS, 1992).
    3) CASE REPORT: Behavioral disturbances (periodic confusion, aggression, confabulations, and secondary encopresis, alternating with normal behavior) developed in an 11-year-old girl who also experienced extensive gingival ulceration, loss of 6 teeth, acrodynia, back pain, anorexia, weight loss, fatigue, tremor, and hypertension following exposure to mercury from a broken industrial thermostatic clock. All laboratory results were normal except for a C-reactive protein of 98 mg/L. Following chelation therapy with DMPS for 9 weeks, she recovered gradually (van der Linde et al, 2009).
    4) CASE REPORT: A 2.5-year-old boy developed lethargy and respiratory distress after exposure to mercury vapors. Following supportive care, including treatment with D-penicillamine, NAC, and multivitamins, he recovered gradually (Sevketoglu et al, 2011).
    B) CENTRAL NERVOUS SYSTEM FINDING
    1) NEUROPSYCHOLOGICAL - Subtle neurological changes in visual-motor function have been associated with elemental mercury exposure (Bluhm et al, 1992a; Lu et al, 1998). Irritability, fatigue, insomnia (Gencpinar et al, 2015; Florentine & Sanfilippo, 1991; Piikivi et al, 1984; Yeates & Mortensen, 1994), depression, and short term auditory memory impairment (Soleo et al, 1990) have been reported.
    2) Self-reported symptoms of poor concentration, loss of appetite, gastrointestinal disturbances, nervousness, sleep disturbances, memory disturbances, and tiredness were greater among 89 chloralkali workers exposed to mercury than 75 unexposed controls (Langworth et al, 1992). The differences in reported tiredness and memory disturbances were statistically significant.
    a) No significant differences between the mercury exposed workers and controls were identified through tremor measurement and administration of a computerized test which measured psychomotor performance, attention, and short term memory. Statistically significant higher neuroticism scores were documented for the chloralkali workers.
    b) A meta-analysis of 36 published studies concluded that neurobehavioral effects from occupational mercury exposure is likely small and difficult to detect on an individual basis (Rohling & Demakis, 2006).
    3) Significantly higher symptoms of fatigue and confusion were reported by workers in a fluorescent lamp factory, when compared to controls (Liang et al, 1993). Individuals in the mercury exposed group had statistically significant decrements in performance of some tasks which involved mental arithmetic, two digit searching, attention switching, visual skills, and finger tapping.
    4) Persistent short-term memory defects, increased reaction time, and defects in motor coordination were seen in a group of former mercury miners, compared with a matched control group, approximately 18 years after the last exposure (Kishi et al, 1994).
    5) Two adolescent children, aged 13 and 15 years, developed more severe neuropsychological symptoms from a 3-month exposure to mercury vapor than did adults under the same circumstances. Defects persisted for at least 1 year (Yeates & Mortensen, 1994).
    6) Mercury poisoning from peritoneal contamination (rupture of a distal balloon weighted with elemental mercury, 10 mL) is reported in a 68-year-old female. Deficits in visuospatial functioning and hand/eye coordination was reported 27 months post exposure. Neurologic symptoms have shown a progression with increased fatigue, decreased memory, insomnia and mild tremor (Lu et al, 1998).
    7) CASE REPORT: A 22-year-old woman presented with a 2-hour history of chest discomfort after injecting herself in the arm with an unknown amount of elemental mercury from 3 thermometers mixed with alcohol. Radiography and CT scans showed radiopaque deposits of mercury mainly in the middle and lower lobes of the lungs bilaterally and in the pericardium, intestine, kidneys, and liver. Laboratory results revealed urine mercury concentrations greater than 60 mcg/L (nontoxic levels: less than 10 mcg/L) and blood concentrations greater than 35 mcg/L (nontoxic levels: less than 6 mcg/L). Despite normal vital signs for 2 to 3 hours, her mental status deteriorated with confusion, disorientation, tremor, and finally stupor (GCS score of 9). She also developed seizures and was treated with diazepam and valproate acid. Following supportive care, including treatment with a dimercaptosuccinic acid (DMSA)/succimer (800 mg orally 3 times daily for 5 days and 600 mg orally 3 times daily for 14 days) and phenytoin (125 mg IV 3 times daily), her mental status improved 2 hours after the initiation of treatment. CT scans of the thorax, abdomen, and brain revealed multiple radiopaque nodes in both lungs, a small pleural effusion, a few mercury deposits on the pericardium, and multiple deposits on the liver, left kidney, spleen and paraspinal muscles. She was discharged 20 days after presentation, but experienced several seizures during the next 6 months. On a 2-year followup, she was stable without additional seizures (Karatapanis et al, 2015).
    8) DIFFERENTIAL DIAGNOSIS (CREUTZFELDT-JAKOB DISEASE): A 42-year-old man presented with a 5-month history of progressive memory disturbance (difficulty in recalling recent conversations), irritability, numbness and tingling in the limbs, slow movement, and sleepiness. Three months before presentation, an MRI of the brain revealed striking, relatively symmetric, high-intensity, diffusion-weighted imaging signals in the cortex without gadolinium enhancement. Slow overall activity was observed in an electroencephalograph. Despite normal results on CSF studies with normal 14-3-3 protein levels, a diagnosis of Creutzfeldt-Jakob disease was made. Although he was treated with IV methylprednisolone and oral prednisone, his condition worsened. On this visit, physical examination revealed prominent cognitive impairment and extrapyramidal features, with bilateral symmetric bradykinesia, cogwheel rigidity in the upper limbs, and impaired finger-nose coordination. A second MRI of the brain showed hyperintense diffusion-weighted imaging signals and hypointense apparent diffusion coefficient signals in the caudate nucleus and the frontal, temporal, and occipital cortices. Laboratory results revealed a blood mercury concentration of 76.3 nmol/L and a urinary mercury concentration of 109.2 nmol/L (reference range, 0 to 12.5 nmol/L). During questioning, it was revealed that the patient cleaned a broken mercury sphygmomanometer in his bed with a whisk broom several days before his symptoms started. Following treatment with sodium 2,3-dimercapto-1-propanesulfonic acid, his numbness and tingling decreased substantially, but memory and movement improved only slightly and no improvement was observed in a follow-up MRI. Persistent cognitive impairment and bradykinesia were observed on a follow-up visit 2 years later. At that time, he had a blood mercury concentration of 2.5 nmol/L and a urinary level of 5.5 nmol/L. An MRI continued to show damage (Tang et al, 2015).
    C) SEIZURE
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 10-year-old boy developed acrodynia, seizures, and visual impairment after exposure to elemental mercury for 20 days. A brain MRI revealed multiple supratentorial hyperintense lesions on T2-weighted images ranging in size from 1 cm to 3 cm in maximum diameter, with lesions located in the cerebral white matter in paracentral gyrus, and left globus pallidus and putamen. Approximately 4 months after the first exposure to elemental mercury, he was diagnosed with mercury poisoning; his whole blood mercury level and the 24-hour urinary mercury level were 27.7 mcg/L (normal <2 mcg/L) and 34.4 mcg/L (normal = 10 mcg/L), respectively. He was treated with dimercaprol (2 courses) and D-penicillamine. Following 35 days of supportive therapy, he was discharged home and followed as an out-patient. He recovered completely after 9 months of treatment without further sequelae (Abbaslou & Zaman, 2006).
    b) CASE REPORT: A 22-year-old woman presented with a 2-hour history of chest discomfort after injecting herself in the arm with an unknown amount of elemental mercury from 3 thermometers mixed with alcohol. Radiography and CT scans showed radiopaque deposits of mercury mainly in the middle and lower lobes of the lungs bilaterally and in the pericardium, intestine, kidneys, and liver. Laboratory results revealed urine mercury concentrations greater than 60 mcg/L (nontoxic levels: less than 10 mcg/L) and blood concentrations greater than 35 mcg/L (nontoxic levels: less than 6 mcg/L). Despite normal vital signs for 2 to 3 hours, her mental status deteriorated with confusion, disorientation, tremor, and finally stupor (GCS score of 9). She also developed seizures and was treated with diazepam and valproate acid. Following supportive care, including treatment with a dimercaptosuccinic acid (DMSA)/succimer (800 mg orally 3 times daily for 5 days and 600 mg orally 3 times daily for 14 days) and phenytoin (125 mg IV 3 times daily), her mental status improved 2 hours after the initiation of treatment. CT scans of the thorax, abdomen, and brain revealed multiple radiopaque nodes in both lungs, a small pleural effusion, a few mercury deposits on the pericardium, and multiple deposits on the liver, left kidney, spleen and paraspinal muscles. She was discharged 20 days after presentation, but experienced several seizures during the next 6 months. On a 2-year followup, she was stable without additional seizures (Karatapanis et al, 2015).
    D) CEREBELLAR DISORDER
    1) WITH POISONING/EXPOSURE
    a) Tremor, ataxia and loss of coordination have been reported in workers chronically exposed to mercury vapor (Albers et al, 1988; Ehrenberg et al, 1991; Donoghue, 1998), in children exposed to mercury vapor in the home (van der Linde et al, 2009; Florentine & Sanfilippo, 1991; Rennie et al, 1999) and in a case of peritoneal mercury contamination (McVittie & Berlin, 1998).
    b) CASE REPORT: A 23-year-old woman presented with dyspnea after injecting herself with 5 mL of elemental mercury. All pulmonary function tests were normal. Following treatment with D-penicillamine for 12 days, she was discharged. She developed disabling generalized myoclonus of cortical origin and gait ataxia 2 years after the initial exposure. She presented with progressive worsening of her handwriting, difficulty placing objects on the table, jerky finger movements at rest that worsened during motor tasks, and severe dysarthria. At this time, her serum mercury level was 6 mcg/dL (normal, 0.06 to 5.9 mcg/dL) and urinary mercury levels were markedly high (80.0 mcg/L; normal, less than 20 mcg/L). Her symptoms progressed over the next 2 years and she presented with a 6-month history of generalized tonic clonic seizures. Her symptoms improved after the mercury deposits were cleared surgically from the injection site (Ragothaman et al, 2007).
    E) SECONDARY PERIPHERAL NEUROPATHY
    1) WITH POISONING/EXPOSURE
    a) Peripheral neuropathy, characterized by decreased strength and sensation, may develop after chronic elemental mercury exposure (Truche et al, 2012; Celebi et al, 2008; Albers et al, 1988; Florentine & Sanfilippo, 1991; Karagol et al, 1998). Signs of axonal neuropathy were seen on electroneuromyography in a 14-year-old boy after several months exposure to elemental mercury (Karagol et al, 1998) and in an 11-year-old girl following exposure to mercury from a broken industrial thermostatic clock (van der Linde et al, 2009). In two additional cases, peripheral neuropathy and hyporeflexia of the lower extremities were reported in adolescents exposed to metallic mercury after playing with broken school barometers (Koyun et al, 2004).
    b) Decreased nerve conduction velocity has been reported in mercury exposed workers without clinical evidence of peripheral neuropathy (Rosenmann et al, 1986).
    F) HYPERREFLEXIA
    1) WITH POISONING/EXPOSURE
    a) Abnormal reflexes (snout, Babinski) were increased in workers with higher urinary mercury excretion compared with their co-workers (Albers et al, 1988).
    G) TREMOR
    1) WITH POISONING/EXPOSURE
    a) Tremors are characteristic of chronic exposure to elemental mercury and typically disappear after exposure has ceased (Schaumburg et al, 2009; van der Linde et al, 2009; US DHHS, 1992). Evaluation of handwriting before and after elemental mercury exposure and treatment can be used to indirectly monitor the adverse effects of exposure and the response to therapy (Yang et al, 1994). Fasciculations of the tongue and legs have been reported in pediatric patients after several months of exposure to elemental mercury (Karagol et al, 1998).
    b) A Parkinsonian syndrome with resting and intention tremor, bradykinesia and cogwheel rigidity have been reported after long term exposure to elemental mercury vapors (Finkelstein et al, 1996). The syndrome improved after penicillamine chelation.
    c) A cross-sectional study of 27 mercury-exposed miners and smelters found higher tremor intensity compared to non-exposed controls. Tests for postural sway did not demonstrate a significant difference between groups. Within exposed workers, tremor intensity did not correlate with urine mercury concentrations. The geometric mean urinary concentration in exposed workers was 228 mcg/g creatinine (Iwata et al, 2007). A similar study of chloralkali workers found no difference in tremor compared to controls. However, the exposed workers in this study had a median urinary mercury concentration of 5.9 mcg/g creatinine (Wastensson et al, 2006).
    H) ELECTROENCEPHALOGRAM ABNORMAL
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: The EEG of a 11-year-old girl showed diffuse slow activity in the first few weeks of mercury poisoning. During chelation therapy, a rapid improvement of this abnormal slowing of the background rhythm was observed (Setz et al, 2008).
    I) ACUTE INTRACRANIAL HYPERTENSION
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 12-year-old boy who was chronically exposed to elemental mercury at home, presented with a 1-month history of severe fatigue, generalized muscle pain, and weakness. On presentation, he had painful extremities, decreased motor strength, and lack of deep tendon reflexes in lower extremities. An electromyography revealed mixed type polyneuropathy. Laboratory results showed elevated whole blood and 24-hour urinary mercury concentrations (23.2 mcg/L [normal: 0 to 10 mcg/L] and 175 mcg/L [normal: 0 to 15 mcg/L], respectively). Despite treatment with succimer which was started on day 4, he developed headache, nausea, bilateral papilledema, and intracranial hypertension 7 days after presentation. Following further supportive care, including treatment with acetazolamide, his condition gradually improved and he was discharged after 35 days of hospitalization with acetazolamide, vitamin B6, and gabapentin (Gencpinar et al, 2015).

Gastrointestinal

    3.8.2) CLINICAL EFFECTS
    A) GASTRITIS
    1) INHALATION
    a) GASTROINTESTINAL DISTRESS: Nausea, vomiting, and diarrhea or constipation can occur after acute mercury vapor inhalation (Cicek-Senturk et al, 2014; Tezer et al, 2012; Sevketoglu et al, 2011; Koyun et al, 2004; Bluhm et al, 1992; Snodgrass et al, 1981; Moutinho et al, 1981; Houeto et al, 1994).
    b) ABDOMINAL PAIN and anorexia are also reported following acute exposure (Florentine & Sanfilippo, 1991; Koyun et al, 2004; Anon, 2005; Bluhm et al, 1992).
    2) INGESTION
    a) Liquid mercury released in the gastrointestinal tract will generally pass through without producing toxicity. Occasionally, the mercury may get hung up in the intestine and may require surgical removal (Cantor, 1951). Systemic absorption has been reported following massive ingestions of mercury.
    b) Mercury may remain in the appendix and produce inflammation (Birnbaum, 1947; Sawyer, 1967; McKinney, 1999) and rupture (Crikelair & Hiratzka, 1953), even in patients without a fistula.
    1) CASE REPORT: A 4-month-old infant presented to the ED with a 4-week history of abdominal "colic" with fever and irritability. Abdominal radiographs showed a metallic density in the right lower quadrant, assumed to be within the appendix. The mother of the patient revealed that the infant had been receiving elemental mercury for 4 to 6 weeks prior to presentation, in order to treat the infant's abdominal pain. A spot blood mercury level was 31 mcg/L. Whole bowel irrigation was unsuccessful in eliminating the mercury, thereby requiring an appendectomy (Miller et al, 2005). Pathology of the appendix indicated retained intraluminal mercury.
    2) CASE REPORT: A 33-year-old woman experienced nausea, vomiting, and abdominal pain after ingestion of approximately 1000 mL (1.3 kg) of elemental mercury. Abdominal x-ray noted a large amount of radiopaque material in the stomach. Follow-up x-rays noted clearance of radiopaque material by 3 weeks post-ingestion. Initial blood and urine mercury concentrations were 180 mcg/L and 653 mcg/L, respectively. No neurological or renal toxicity was reported (Song & Li, 2007).
    3) CASE REPORT: A 43-year-old man presented to the ED with severe abdominal pain and persistent vomiting following the ingestion of 200 mL of elemental liquid mercury in a suicide attempt. His chest x-ray revealed small amounts of mercury in lower lung fields bilaterally, indicating aspiration. He was treated with IV fluids, opioid analgesics, and antiemetic medications before being transferred to a negative pressure side room to reduce the risk of mercury inhalation by hospital staff. A nasogastric tube was inserted and 115 mL of mercury was aspirated from his stomach leading to significant improvement in patient's symptoms and resolution of vomiting. The patient's blood mercury concentrations continued to rise by day 2 (675 nmol/L on admission and 934 nmol/L on day 2), suggesting continual systemic absorption from the lungs and his 24-hour urine mercury concentration was also elevated (14365 nmol/day). At this time, he was treated with IV 2,3-dimercaptopropane-1-sulfonate (DMPS, Dimaval; 30 mg/kg/day in 8 divided doses for 6 days), leading to improved blood and urinary mercury concentrations that continued to decrease 5 days later. The patient was subsequently discharged home after psychiatric review (Dawson et al, 2013).
    3) INJECTION
    a) CASE REPORT: Mild gastrointestinal disturbances developed in a man after the intravenous injection of 3 mL of elemental mercury and ingestion of 3 mL in a suicide attempt (McFee & Caraccio, 2001).
    b) CASE REPORT: A 42-year-old woman presented with a 2-year history of painful violaceous nodules and plaques on her right forearm and left anterior tibia. The patient who was injecting mercury to these sites for several years to treat HIV infection, also experienced nausea, vomiting, chronic nonlocalizing abdominal pain, weakness, headaches, and visual disturbances. Laboratory results showed a serum mercury concentration of 300 mcg/L (reference range, less than 5 mcg/L). Despite treatment with penicillamine for 3 months, her serum mercury concentration did not decrease. Her symptoms improved after intraoperative C-arm fluoroscopy-assisted surgical debridement of the areas (Altmeyer et al, 2011).
    B) HEMORRHAGIC COLITIS
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 46-year-old man presented with fever, sharp abdominal pain, bloody diarrhea, and tachycardia 5 days after exposure to mercury vapor during purification of gold from a mercury-containing ore in his home. Physical examination revealed hypoactive bowel sounds and diffuse tenderness to palpation over the abdomen. An abdominal CT revealed diffuse colonic wall thickening and thumbprinting, especially in the ascending colon, consistent with colitis. Colonoscopy showed severe erythema and friability in distal colon. Following supportive treatment, including dimercaprol therapy for 3 weeks, his symptoms improved gradually (Heise et al, 2009).

Hepatic

    3.9.2) CLINICAL EFFECTS
    A) LIVER DAMAGE
    1) Mild jaundice and abnormal liver function tests developed in an adult male six months after ingestion of metallic mercury. The individual was also chronically exposed to mercury in his occupation. The authors propose a contribution of slowly absorbed mercury to delayed hepatic dysfunction (Lin & Lim, 1993).
    2) Hepatomegaly developed in a A 52-year-old woman after exposure to mercury fumes (Cicek-Senturk et al, 2014).
    B) CHOLECYSTITIS
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 53-year-old man underwent cholecystectomy for a suspected gall bladder wall mass. Biopsy noted droplets of elemental mercury within chronically inflamed tissue. The patient had previously attempted suicide by intravenous injection of elemental mercury at the age of 18 (Zippel et al, 2006).

Genitourinary

    3.10.1) SUMMARY
    A) Mercury vapor exposure may result in proteinuria or nephrotic syndrome. Acute tubular necrosis and renal failure may develop. Dysuria and ejaculatory pain have been reported following acute exposure. Transient abnormalities in urinary electrolytes may occur.
    3.10.2) CLINICAL EFFECTS
    A) ALBUMINURIA
    1) Proteinuria has been reported after acute mercury vapor exposure (Snodgrass et al, 1981; Karagol et al, 1998).
    B) RENAL TUBULAR DISORDER
    1) Reversible renal tubular defects were found in 11 men acutely exposed to mercury vapor and in miners chronically exposed to mercury vapor for an average of 15 years. Hyperchloremia, low normal serum bicarbonate, a normal serum anion gap and an elevated urine anion gap were found in these patients (Franko et al, 2005; Bluhm et al, 1992).
    2) LACK OF EFFECT: A study of 49 chloralkali workers with previous occupational mercury exposure found no difference in renal function compared to controls. Mercury exposure had ceased an average of 4.8 years prior to the study in these workers (Efskind et al, 2006).
    C) RENAL FAILURE SYNDROME
    1) WITH POISONING/EXPOSURE
    a) Acute renal failure has been reported in one patient who inhaled smoke from dried lime which contained elemental mercury (Mohan et al, 1994). The mercury containing lime was burned with leaves as a folk medicine.
    b) CASE REPORT: A 62-year-old man developed cough, dyspnea, and lethargy after attempting to extract gold from an amalgam containing mercury by heating the amalgam in an aluminum pan. He was exposed for 3 hours via fumes and through direct skin contact. A chest x-ray revealed extensive alveolar shadowing indicating pneumonitis. Laboratory findings revealed blood mercury concentration of 5933 nmol/L (level of concern: greater than 70 nmol/L), an elevated white cell count (16.3 x 10(9)/L, reference interval [RI]: 4 to 11 x 10(9)/L), a platelet count of 617 x 10(9) (RI 150 to 400 x 10(9)/L), an abnormal serum albumin concentration (21 g/L, RI: 34 to 48 g/L), and mildly elevated liver enzymes. A urinalysis revealed a mercury concentration of 7556 nmol/L and the mercury:creatinine ratio of 2519 nmol/mmol (level of concern: greater than 5.8 nmol/mmol). Following supportive care, including treatment with dimercaptosuccinic acid (DMSA) (800 mg 3 times daily for 7 days followed by a dose reduction to 800 mg twice daily for an additional 14 days) and prednisolone (50 mg daily with a gradual dose taper down to zero over 3 weeks), his symptoms gradually resolved. A 3-week re-assessment showed ongoing elevated blood mercury concentrations (blood mercury 418 nmol/L), therefore he was re-challenged with DMSA 800 mg 3 times daily for 34 days (starting 66 days after exposure). Despite the improvement of symptoms following prolonged course of DMSA, he re-presented with fatigue, increasing peripheral edema, nausea, and vomiting. Biochemical analysis revealed severe nephrotic syndrome and he was subsequently treated with prednisolone, regular infusions of concentrated albumin, diuretics, and was restricted to 1.2 L of fluids daily. His condition gradually normalized over the next 4 months (Saleem et al, 2013).
    D) DYSURIA
    1) Dysuria and ejaculatory pain without concomitant evidence of urologic disease developed in workers acutely exposed to toxic levels of mercury vapor (Bluhm et al, 1992a).
    E) ABNORMAL RENAL FUNCTION
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: Minor elevations in BUN (28 mg/dL), serum creatinine (2 mg/dL) and decreased urine output developed in a man after the intravenous injection of 3 mL of elemental mercury and ingestion of 3 mL in a suicide attempt (McFee & Caraccio, 2001).
    F) DYSMENORRHEA
    1) WITH POISONING/EXPOSURE
    a) A retrospective epidemiological Chinese study of 296 female workers (18 to 44 years of age) exposed to mercury vapor and 394 female workers (control group) from food processing plants showed a significantly higher prevalence of dysmenorrhea (odds ratio (OR) = 1.66, 95% CI 1.07 to 2.59) and abdominal pain (OR = 1.47, 95% CI 1.03-2.11) in the exposed group compared to the control group. The workplace air concentration of mercury ranged from 0.001 to 0.2 mg/m(3) (Yang et al, 2002).
    G) RENAL ARTERY EMBOLISM
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 34-year-old man presented with fever, vomiting, and hemoptysis 2 days after the self-injection of 25 mL of elemental mercury in a suicide attempt. On presentation, his plasma mercury concentration was 2625 mcg/L (upper limit of normal: 15 mcg/L). A chest x-ray revealed several metallic densities throughout both lung fields, with numerous mercury deposits in the pulmonary venous circulation, and in the right auricular and ventricular cavities. An abdominal x-ray revealed mercury embolism of renal arteries. Following the excision of all affected subcutaneous tissues, he received dimercaptosuccinic acid (10 mg/kg 3 times daily for 15 days); however, his blood mercury concentration did not decrease significantly. His serum creatinine concentrations were between 70 to 80 mcmol/L during the first month and it increased to 164 mcmol/L 2 years post-exposure. Within the next 3 years, he developed recurrent subcutaneous abscess with droplets of mercury, sensory motor polyneuropathy, and a toxic megacolon complicated by peritonitis. He was started on hemodialysis 4 years after exposure and remained hemodialysis dependent 12 years after exposure (Truche et al, 2012).

Hematologic

    3.13.2) CLINICAL EFFECTS
    A) THROMBOCYTOPENIC DISORDER
    1) Thrombocytopenia has been reported in children and adults exposed to elemental mercury vapors (Schwartz et al, 1992; Fuortes et al, 1995).
    B) ANEMIA
    1) Anemia and lymphopenia developed in one woman who, as a folk medicine practice, inhaled smoke from burning dried lime which contained elemental mercury (Mohan et al, 1994).
    a) The duration and frequency of the elemental mercury exposure was unknown. Smoke from the burning of a red dust and dried leaves (substances not identified) were also inhaled.
    2) CASE REPORT: A 30-year-old woman presented with mercury toxicity after self-injection and ingestion of approximately 500 g of mercury from 37 broken fever thermometers. Despite supportive treatment, she developed lung embolization complicated by acute respiratory distress syndrome (ARDS), toxic dermatitis, anemia (hemoglobinemia less than 7.1 g/dL), and mild hepato-renal impairment, and died 30 days after presentation (DePalma et al, 2008).
    C) ERYTHROCYTE ENZYME DEFICIENCY
    1) Chronic mercury exposure in exposed workers resulted in changes in glucose-6-phosphate dehydrogenase (G6PD), acetylcholinesterase, glutathione reductase, and superoxide dismutase, as well as increases in hematocrit and decreases in MCV, MCHC, and ferritin (Zabinski et al, 2000).
    D) LEUKOCYTOSIS
    1) WITH POISONING/EXPOSURE
    a) CASE REPORTS: A 52-year-old woman presented with a 15-day history of high fever (39 degrees C on presentation), sore throat, itchy rash, generalized muscle pain, and nausea. Her husband and son had similar symptoms. Despite treatment with penicillin G, antihistaminic and antipyretic agents, and depot steroid treatments, her condition did not improve. Physical examination revealed a generalized maculopapular rash over her entire body, and bilateral cervical and axillary painful and mobile lymphadenopathies. Laboratory results revealed elevated serum urea, serum creatinine, lactate dehydrogenase, total protein, albumin, WBC, and C-reactive protein and decreased hemoglobin. Hepatomegaly was observed in an abdominal ultrasonography. A chest radiography showed several uncertain modular lesions. After several days of symptomatic treatment while trying to exclude malignancies and infectious and autoimmune diseases, it was revealed that the patient's son had brought mercury home from school. The family was exposed to mercury fumes after he spilled the mercury on the hot stove. About 10 hours later, her husband developed dyspnea, hypertension, tachycardia, high fever, and sore throat. Laboratory results revealed leucocytosis. Following supportive care, his symptoms improved and he was discharged after 8 days of hospitalization, but he developed a personality disorder several days later. Her son developed high fever, sore throat, skin rash, diarrhea, dyspnea, a generalized maculopapular rash, hyperemia in the conjunctivas, cervical bilateral axillary lymphadenopathy, and leukocytosis after exposure to mercury fumes. All patients were treated with penicillamine 300 mg every 6 hours for 7 days (Cicek-Senturk et al, 2014).

Dermatologic

    3.14.2) CLINICAL EFFECTS
    A) SKIN ABSORPTION
    1) WITH POISONING/EXPOSURE
    a) Liquid elemental mercury and mercury vapors can be absorbed through the skin to a limited degree. Skin absorption of mercury is much less than absorption which may occur through the lungs (Hursh et al, 1989; US DHHS, 1992).
    b) CASE REPORT: An intern aboard an ore boat was inadvertently exposed to elemental mercury liquid following a spill and was likely initially exposed to mercury vapors (due to the extremely warm environment and improper clean-up of the spill). Despite eventual environmental clean-up and removal of his contaminated clothing, the patient continued to wear the same boots, which were visibly contaminated with mercury, up to two weeks after the initial exposure. Because the patient developed laboratory evidence (a peak mercury serum level of 188.8 ng/mL 16 days after exposure) and symptoms of mercury exposure (complaints of nervousness and tremor), the authors speculated that cutaneous absorption of the vapor may have contributed to the patient's elevated serum mercury levels (Roach & Busch, 2004).
    B) ERUPTION
    1) WITH POISONING/EXPOSURE
    a) Erythematous macular or papular rashes are common with mercury vapor poisoning. The rash usually involves the hands and feet. The trunk, axillae, popliteal and antecubital fossae may also be affected (Cicek-Senturk et al, 2014; Tezer et al, 2012; Agner & Jans, 1978; Bartolo & Brandao, 1988; Bluhm et al, 1992; Fuortes et al, 1995).
    b) Miliary pustules, petechial erosions and exfoliation can develop (Horn & Burnett, 1988).
    c) CASE REPORT: A generalized maculopapular erythematous rash has been reported from inhalation of smoke from a burning folk medicine which contained elemental mercury (Mohan et al, 1994).
    C) CONTACT DERMATITIS
    1) WITH POISONING/EXPOSURE
    a) Allergic contact dermatitis from handling metallic mercury has been reported (Goh & Ng, 1988; Kanerva et al, 1993; Faria & De Freitas, 1992). A dermatitis with papular erythema can result from skin exposure to liquid elemental mercury (US DHHS, 1992).
    b) Two patients experienced mercury-induced relapsing nummular dermatitis with multiple exudative erythematous-plaques. Patch tests of both patients showed hypersensitivity to 1% ammoniated mercuric chloride, as well as 0.05% mercuric chloride. Skin eruptions improved significantly after the removal of the amalgam from dental metal alloys. One patient, a 32-year-old dentist, experienced a sudden relapse with eruptions on his lower legs 24 hours after handling the dental amalgam alloys in his dental clinic (Adachi et al, 2000).
    D) ACRODYNIA DUE TO MERCURY
    1) WITH POISONING/EXPOSURE
    a) ACRODYNIA: Subchronic or chronic mercury poisoning may rarely result in acrodynia. The syndrome is characterized by severe leg cramps, pink, painful, and peeling skin of the fingers, hands, feet, and nose (Mercer et al, 2012; van der Linde et al, 2009; Celebi et al, 2008; US DHHS, 1992). Although acrodynia may occur in adults (Gosselin et al, 1984), it is more common in children (US DHHS, 1992; Karagol et al, 1998).
    b) CASE REPORT: Acrodynia, along with other symptoms of mercury intoxication, were reported in two children following exposure to metallic mercury; the source was broken barometers taken from school laboratories. Blood and urine levels confirmed the presence of elevated mercury levels (Koyun et al, 2004).
    c) CASE REPORT: Symptoms of acrodynia including marked hypertension (BP 162/100 mmHg) were reported in a 3-year-old male. Diagnosis was not confirmed until his younger sibling presented with similar symptoms. Blood mercury levels were markedly elevated in each child (112.2 and 54.8 {normal range 0 to 11.3 nmol/L}, respectively). High levels of mercury were found in the carpet of the child's room, although no source could be identified. Of note, the parents had the lowest levels of exposure. Chelation therapy with DMSA was effective in improving clinical symptoms, but mercury levels took almost 2 years to completely normalize. Long-term effects are as yet unknown(Beck et al, 2004).
    d) CASE REPORT: Acrodynia developed in a 10-year-old boy after exposure to elemental mercury for 20 days. He experienced acral papular rash, pruritus, bloody diarrhea, severe bone pain in the lower extremities (especially knees), paresthesia, diaphoresis, irritability, palpitations, and insomnia. In addition, he experienced generalized seizures, transient blurred vision, headache, diplopia, and hypertension (BP 170/120 mmHg). A brain MRI revealed multiple supratentorial hyperintense lesions on T2-weighted images ranging in size from 1 cm to 3 cm in maximum diameter, with lesions located in the cerebral white matter in paracentral gyrus, and left globus pallidus and putamen. Approximately 4 months after the first exposure to elemental mercury, he was diagnosed with mercury poisoning; his whole blood mercury level and the 24-hour urinary mercury level were 27.7 mcg/L (normal <2 mcg/L) and 34.4 mcg/L (normal = 10 mcg/L), respectively. He was treated with dimercaprol (2 courses) and D-penicillamine. Following 35 days of supportive therapy, he was discharged home and followed as an out-patient. He recovered completely after 9 months of treatment without further sequelae (Abbaslou & Zaman, 2006).
    E) ALOPECIA
    1) WITH POISONING/EXPOSURE
    a) Mild hair loss has been reported following peritoneal contamination from elemental mercury (Lu et al, 1998).
    F) GRANULOMA
    1) WITH POISONING/EXPOSURE
    a) Granuloma formation with fibrosis and inflammation has developed after intravenous mercury injection (Schaumburg et al, 2009; Netscher et al, 1991), as well as subcutaneous, and intramuscular injections (Kern et al, 1972; Makalinao et al, 1995; Bradberry et al, 1996). Cutaneous mercury granuloma has developed following an accidental occupational injury from a mercury thermometer. Local effects after an accidental inoculation of metallic mercury include erythema, indurated nodules and plaques with or without ulceration. Systemic effects (ie, acute respiratory failure, renal failure, neurologic and psychiatric problems) may also occur following gradual absorption from the inoculation site (George et al, 2015).
    b) CASE REPORT: A 42-year-old woman presented with a 2-year history of painful violaceous nodules and plaques on her right forearm and left anterior tibia. The patient who was injecting mercury to these sites for several years to treat HIV infection, also experienced nausea, vomiting, chronic nonlocalizing abdominal pain, weakness, headaches, and visual disturbances. Radiographic examination showed metallic particles in subcutaneous tissue in the injection sites. Biopsy of the lesion on the right forearm revealed a foreign body granulomatous reaction around black opaque globules. Laboratory results showed a serum mercury concentration of 300 mcg/L (reference range, less than 5 mcg/L). Despite treatment with penicillamine for 3 months, her serum mercury concentration did not decrease. Her symptoms improved after intraoperative C-arm fluoroscopy-assisted surgical debridement of the areas (Altmeyer et al, 2011).
    c) CASE REPORT: Granuloma and abscesses developed in a child after breaking a thermometer in his mouth and another after falling on a thermometer. Glass and mercury were deposited in the soft tissues (Sau et al, 1991; Smith et al, 1997).
    d) Systemic absorption can occur from mercury imbedded in soft tissue and excision with removal of as much mercury as possible is recommended (Netscher et al, 1991; Bradberry et al, 1996; Tanaka et al, 1997).
    1) CASE REPORT: High urinary mercury levels were detected in a man who had developed granuloma after subcutaneously injecting elemental mercury (Kern et al, 1972). The possibility of inhalation of mercury vapors cannot be ruled out in this case. The man was asymptomatic.
    G) INJECTION SITE NECROSIS
    1) CASE REPORT: A 41-year-old female with a history of schizophrenia intentionally subcutaneously injected metallic mercury into her wrist and antecubital fossa. The presence of mercury was confirmed by radiography and ultrasound scan and soft tissue injury was evident within 3 days of injection. Treatment included surgical intervention to remove the mercury streaks contained in the muscle belly and brachialis, as well as friable necrotic tissue that developed along the tract. Chelation therapy with dimercaprol and 2,3-dimercaptosuccinic acid was also performed due to elevated blood and urine levels. Blood mercury levels decreased from 101 to 151 nmol/L in the first two weeks of exposure to 42 nmol/L approximately 3 months later (Soo et al, 2003).
    2) CASE REPORT: Membranous fat necrosis has been reported in an individual with intentional subcutaneous mercury injection (Ramdial et al, 1999).
    H) LICHENOID DERMATITIS
    1) WITH POISONING/EXPOSURE
    a) Eighty-four patients presented with reticulate, lacy, plaque-like or erosive oral lichenoid changes adjacent to amalgam fillings. Multiple treatments (eg; topical, intralesional, and oral corticosteroids, retinoids and topical antifungals) were ineffective. Patch testing to metallic mercury, 0.1% thimerosal, 1% ammoniated mercury, 0.1% mercuric chloride, 0.05% phenylmercuric nitrate or amalgam discs were positive in 33 (39%) patients. The amalgam fillings were replaced with composite resin, gold, porcelain, or a combination of these in 30 of the 33 patch test positive patients. Improvement of signs and symptoms were observed in 28 (87%) patients (Wong & Freeman, 2003).

Musculoskeletal

    3.15.2) CLINICAL EFFECTS
    A) TOXIC EFFECT OF MERCURY AND/OR ITS COMPOUNDS
    1) Elevated blood and urinary mercury levels have been reported following intramuscular injection of metallic mercury (Makalinao et al, 1995).
    B) ACUTE POLYARTHRITIS
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 48-year-old man presented with a 3-day history of severe polyarthritis (diffuse joint pain of shoulders, elbows, wrists, hands, knees and feet) and dysphagia after exposure to mercury vapors 11 days before admission. Laboratory results showed an elevated erythrocyte sedimentation rate of 65 mm/h and C-reactive protein of 48 mg/L, with a normal complete blood count. Twelve days after the exposure, his blood mercury level was 15.2 (reference, less than 10 mcg/dL). Following supportive care, his symptoms resolved within 7 days (Karatas et al, 2002).
    C) LOW BACK PAIN
    1) WITH POISONING/EXPOSURE
    a) Lumbago has been reported in a 11-year-old girl with mercury poisoning (Setz et al, 2008).

Endocrine

    3.16.2) CLINICAL EFFECTS
    A) HYPERTHYROIDISM
    1) Two cases of hyperthyroidism associated with mercury vapor intoxication have been reported (Karpathios et al, 1991; McCann et al, 1991).
    B) PHEOCHROMOCYTOMA
    1) WITH POISONING/EXPOSURE
    a) Signs and symptoms of pheochromocytoma (hypertension, diaphoresis, tremor, irritability and insomnia) and elevated plasma and urinary catecholamine levels developed in a 14-year-old chronically exposed to mercury vapor from a contaminated electric coil heater (Henningsson et al, 1993). Similar symptoms (eg; hypertension, irritability, fatigue, diaphoresis and weight loss) were reported in a 3-year-old male chronically exposed to high mercury levels found in the carpet of his room (the source was never determined) and were thought to be related to pheochromocytoma . However, the child also exhibited erythema and pruritus of his palms and soles (Beck et al, 2004).
    b) CASE SERIES: Five brothers (ages, 2, 5, 7, 9, and 18 years) presented with a 6-month history of pheochromocytoma-like signs and symptoms (hypertension, tachycardia, headache, abdominal pain, leg pain, lassitude, diaphoresis, weight loss). The patients received captopril (2 mg/kg/day) to treat hypertension. In all cases, laboratory analysis revealed elevated vanillylmandelic acid (VMA) in 24-hour urine specimens. After 4 days of treatment with captopril, serum and urine mercury levels were found to be significantly elevated. At this time, one patient admitted to taking a handful of mercury from a science laboratory at school, which the children had played with and spilled on carpet. After one month of therapy with D-penicillamine at 30 mg/kg/day and nifedipine at 2 mg/kg/day, all patients recovered and their urinary mercury and VMA levels were within normal limits (Kosan et al, 2001).

Immunologic

    3.19.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) GLOMERULONEPHRITIS
    a) Animal studies reviewed by Ellingsen et al (1993c; 1994) report the development of mercuric chloride induced, immune complex mediated glomerulonephritis (Ellingsen et al, 1993c; Ellingsen et al, 1994). Not all species or strains of animals are susceptible to mercury induced glomerulonephritis.
    2) ANTINUCLEAR FACTOR TEST POSITIVE
    a) Early signs of renal effects in rats included production of autoantibodies to the glomerular basement membrane.
    3) WBC ABNORMAL
    a) PMN LEUKOCYTES - In vitro models have demonstrated that inorganic and organic mercury may hamper the bacteriocidal activity of polymorphonuclear leukocytes (Obel et al, 1993).

Reproductive

    3.20.2) TERATOGENICITY
    A) SUMMARY OF HUMAN DATA
    1) The possible effects on the human fetus as a result of elemental mercury exposure have not been thoroughly studied (US DHHS, 1992). The evidence linking elemental mercury exposure to developmental or teratogenic effects in humans is less clear than in the cases of organic mercury exposure. Many of the human studies have involved exposure to other chemicals in addition to elemental mercury.
    2) There is evidence that mercury can cross the placenta and is excreted in breast milk. There have been some reports of adverse reproductive effects in human females and males exposed to elemental mercury.
    B) SUMMARY OF ANIMAL STUDIES
    1) Some animal studies have shown that vapors may cause embryotoxicity, fetotoxicity, and other adverse reproductive outcomes. The relevance of these studies to humans is unclear (US DHHS, 1992). There is little evidence of teratogenic effects due to elemental mercury. Several animal studies report adverse effects on male and female fertility or reproductive organs as a result of elemental mercury exposure.
    2) Animal studies have reported adverse reproductive effects as a result of organic or inorganic (e.g. salts) mercury exposure.
    C) CASE STUDIES
    1) SUMMARY - Studies concerning the effects of occupational exposure to elemental mercury during pregnancy have conflicting results.
    2) A Finnish national study listed mercury among the substances associated with CNS defects, cleft palate, and skeletal defects (Kurppa et al, 1983).
    3) A study of 209 mercury-exposed workers failed to find significant neuropathies associated with prenatal exposure (Klimkova-Deutschov, 1977).
    4) A woman was exposed in the home to mercury vapor prior to pregnancy and through the 17th week of gestation (Thorp et al, 1992). Mercury concentrations in the home were 20 to 60 mcg/m(3).
    a) A 24 hour urinary mercury level was 230 mcg/L. The house was decontaminated and a normal infant was born at term. Elevated hair mercury levels were detected in the neonate's hair. No developmental abnormalities were detected in the child at a 2 year medical follow-up.
    5) Lien et al (1983) reported a case of acute mercury toxicity following vapor inhalation by a pregnant woman. Twenty-six days after the exposure, a child was born without clinical abnormalities, but with serum mercury levels comparable to those of the mother.
    6) LIMITATIONS OF HUMAN STUDIES
    a) Many of the human studies involve exposure to other chemicals in addition to mercury. The contribution of mercury alone to the adverse reproductive effects is difficult to determine.
    b) The occupational studies reporting effects of mercury on the female reproductive system and on abortion incidence need further clarification as to the nature and extent of the exposures (Barlow & Sullivan, 1982).
    D) PLACENTAL BARRIER
    1) CASE STUDIES
    a) Studies have shown that various forms of mercury reach the fetus via the placenta. Some forms of mercury can be concentrated in the placenta, resulting in decreased exposure of the fetus.
    b) Some studies have reported no barrier to (total) mercury transfer across the placenta (Lauwerys et al, 1978) Tsucyiya et al, 1984). Other investigators conclude that the placenta may act as a barrier to mercury (Rosival, 1984). Roels et al (1978) reported that the placenta does not concentrate mercury.
    2) TRANSPLACENTAL HG TRANSFER
    a) CASE REPORTS
    1) Acute inhalation of mercury vapor by pregnant women has resulted in comparable mercury levels in maternal and newborn blood (Lien et al, 1983).
    2) Comparable levels of mercury have been found in the mother, fetus and placenta (Baglan, 1974).
    3) In one case, a pregnant woman was exposed to concentrations of 20 to 60 mcg/m(3) in her house from mercury spilled on the carpet. Exposure was during the first 17 weeks of gestation. Further exposure did not occur after the problem was detected. At birth, mercury was present at 16.2 ng/g in the placenta, 1.4 ng/mL in cord blood, and was undetectable in the maternal blood (Thorp et al, 1992).
    4) Total mercury has been detected as early as five weeks gestational age (Nishimura et al, 1974). The level of mercury in the placenta and fetal membranes was higher in women occupationally exposed to mercury below the TLV than in unexposed women (Wannug, 1975) Wanag & Skjaerasen, 1975).
    5) Maternal and neonatal hair samples were obtained from 82 subject pregnancies of which 27 had received maternal dental amalgams during gestation. Maternal and neonatal hair mercury concentrations were 0.39 microg/g (range 0.1-2.13) and 0.24 microg/g (range 0.1-1.93), respectively. Dental restoration was associated with a statistically higher level of maternal and neonatal hair mercury (Razagui & Haswell, 2001).
    6) Amniotic fluid mercury concentrations did not relate to number of amalgam fillings, but did relate to the occurrence of dental amalgam repairs (Luglie et al, 2000).
    3) HUMAN STUDY LIMITATIONS
    a) Some studies of the mercury concentrations in maternal and fetal biological samples have not differentiated between inorganic and organic mercury. Total mercury, rather than organic or inorganic mercury, has only been reported in many studies. Exact exposure sources and doses have not been clearly identified.
    b) The contribution of exposure to other forms of mercury cannot be ruled out in many studies. Dietary methyl mercury, for example, is a key source of non-occupational mercury exposure in the general population, and can contribute to fetal mercury exposure (US DHHS, 1992).
    4) RISK FACTORS
    a) FACTORS INFLUENCING TRANSPLACENTAL TRANSFER: Concentrations of maternal proteins which bind mercury and the order of the pregnancy (eg, first or later pregnancy) may determine how easily mercury is transferred through the placenta (Leffler P & Nordstroem S, 1983).
    5) ANIMAL STUDIES
    a) TRANSPLACENTAL HG TRANSFER
    1) SUMMARY: Several animal studies have shown that maternal exposure to elemental mercury may result in greater exposure of the fetus than occurs with maternal exposure to inorganic mercury.
    b) RATS
    1) A study compared the placental transfer of elemental mercury to the transfer of mercuric chloride (inorganic mercury) after intravenous injection and vapor inhalation in rats. The study showed a 40-fold greater transplacental transfer of mercury to the fetus after maternal elemental mercury vapor exposure, compared to fetal exposure to mercury after maternal injection of mercuric chloride. Placental concentrations of mercury, however, were greater with mercuric chloride exposure than with elemental mercury exposure(Clarkson et al, 1972).
    2) Another study similarly showed that the rat fetus had greater mercury exposure following maternal inhalation of elemental mercury vapor than with maternal inorganic mercury injection (Greenwood et al, 1972).
    c) EWES - Vimy et al (1990) reported the transfer of mercury to fetal blood and amniotic fluid 2 days after placement of dental amalgams in pregnant ewes. Mercury from the amalgams concentrated principally in the fetal liver and pituitary gland tissues as gestation progressed. Placental mercury concentrations also increased with the advancement of gestation.
    E) ANIMAL STUDIES
    1) RATS
    a) Exposure of rats to mercury on day 2 to day 20 of pregnancy resulted in increased resorption of fetuses, higher incidence of growth retardation among the pups, and 100% pup mortality prior to weaning (Baranski, 1973).
    b) Embryotoxicity and increased postnatal pup mortality has been reported in rats following chronic exposure to mercury vapor (Ignatev, 1980).
    c) Chronic exposure of rats during pregnancy was associated with altered immunological activity in the offspring and in the second generation offspring (Goncharuk, 1971).
    2) MOUSE
    a) Maternal exposure to mercury at 0.23 or 2.1 mg per m(3) resulted in fetotoxicity in the mouse (Selypes, 1983).
    3) MONKEYS
    a) Mercury was a weak teratogen in cynomologus monkeys (Grant, 1982), and was not eliminated by the fetus (Clayton & Clayton, 1982).
    3.20.3) EFFECTS IN PREGNANCY
    A) ABORTION
    1) CASE REPORTS
    a) Women exposed to an average of 0.08 mg per m(3) reportedly had more problems during pregnancy and had increased incidence of spontaneous abortion (Goncharuk, 1971; Panova & Ivanova, 1976).
    b) Mercury was among the many chemicals at a refinery where wives of workers were at increased risk for miscarriage and stillbirths (Anon, 1982). These effects could not be attributed to any single chemical.
    c) Among female dental assistants who were exposed to mercury and nitrous oxide, there was no increase in spontaneous abortions (Heidam, 1984).
    d) There have been reports of syphilis patients who were treated with mercury having an increased incidence of spontaneous abortions. The effects of mercury alone are not clear (Barlow & Sullivan, 1982).
    e) One study reported the risk of spontaneous abortion, determined by questionnaires, was significantly associated with paternal exposure to mercury. Paternal exposure was confirmed by monitoring of urinary mercury levels. Exposure to heat, chlorine, soda, hydrogen, and sulfuric acid also occurred, but reportedly did not influence the rate of spontaneous abortions (Cordier et al, 1992).
    B) PREGNANCY DISORDER
    1) Women exposed to mercury reportedly had anemia, early toxicosis, bleeding, prolonged labor, and lower birth weights (Vasileva, 1975; Mishonova et al, 1980; Gelbier & Ingram, 1989). Complicated pregnancies have been reported in another study of women with combined exposures to mercury, lead, benzene and carbon disulfide (Vasileva, 1975).
    C) OTHER NON-SPECIFIC
    1) LIMITATIONS OF HUMAN STUDIES - Many of the human studies involve exposure to other chemicals in addition to mercury. The contribution of mercury alone to the adverse reproductive effects is difficult to determine.
    2) The occupational studies reporting effects of mercury on the female reproductive system and on abortion incidence need further clarification as to the nature and extent of exposures (Barlow & Sullivan, 1982).
    D) LACK OF EFFECT
    1) CASE REPORTS
    a) A 17-year-old woman injected approximately 3 mL of liquid metallic mercury into her left antecubital vein in a suicide attempt. Ten years later she became pregnant, at that time she had no symptoms but had persistently elevated mercury concentrations. Mercury concentrations at the beginning of pregnancy were: serum 216 ng/mL; urine 413 ng/mL; whole blood 209 ng/mL. Despite these high levels, the mother did not experience any neurological sequelae or long-term toxic damage from mercury exposure. She delivered a healthy baby girl. At the time of delivery, mercury concentrations were as follows: maternal serum 189 ng/mL, maternal urine 241 ng/mL, breast milk 281 to 318 ng/mL, placental tissue 1,111 ng/g, placental blood 127 ng/mL, serum from umbilical cord 145 ng/mL, umbilical cord whole blood 190 ng/mL, amniotic fluid 8 ng/mL. On several follow-up visits, the infant's developmental neurobehavioral milestones and growth were appropriate for her age (Pugach & Clarkson, 2009).
    b) One study reported the full term birth of an apparently normal male infant after significant exposure of the mother to elemental mercury before pregnancy and during the first trimester of pregnancy. The mother was exposed to vapors in the home from spilled elemental mercury. The exact duration of exposure was not reported. The mother was asymptomatic. Mercury vapor concentrations were 20 to 60 mcg/m(3), which were above the EPA suggested air concentrations (at the time of the report) of less than 1 mcg/m(3). Maternal 24 hour urinary mercury concentrations were 230 mcg/L at initial examination, decreasing during gestation to 7.5 mcg/L at 24 weeks, 2.7 mcg/L at 33 weeks, and undetectable at 36 weeks. An apparently healthy male was delivered full term. Mercury concentrations of the placenta and neonatal hair (3 ng/g; normal less than 0.0008) at birth were above the normal levels expected with no mercury exposure. Mercury levels in the maternal and cord blood were within the normal range. At 2 years of age, the child was of appropriate growth and had met the appropriate developmental milestones. Formal psychodevelopmental testing was not performed (Thorp et al, 1992a).
    E) ANIMAL STUDIES
    1) Exposure of rats on day 7 to 20 of pregnancy has resulted in increased resorption of fetuses, pup growth retardation and 100% mortality of pups prior to weaning (Baranski, 1973).
    2) Mercury vapor exposure resulted in changes in estrus cyclicity but no other changes in reproductive performance in rats (Davis et al, 2001). These changes occurred only at the highest dose tested (4 mg/m3 for 2 hours per day for 11 consecutive days) and was associated with weight loss.
    3.20.4) EFFECTS DURING BREAST-FEEDING
    A) STUDIES
    1) In a study of 155 lactating Saudi mothers, the mean concentration of mercury in breast milk was 1.19 mcg/L (range, 0.012 to 6.44 mcg/L), with 57.4% (n=89) of mothers having mercury levels at or above 1 mcg/L, which is the background level for mercury in human milk. All mothers had total blood mercury concentrations below the US Environmental Protection Agency's maximum reference dose of 5.8 mcg/L. Mercury in breast milk was significantly correlated with mercury in maternal blood (p less than 0.001), suggesting efficient transfer of mercury from blood to milk. Measured as biomarkers of oxidative stress, urinary 8-hydroxy-2'-deoxyguanosine (8-OHdG) and malondialdehyde (MDA) increased with increasing levels of mercury in breast milk and urinary mercury levels in infants in a dose-related manner. Thus, the exposure to mercury in breastfed infants may induce oxidative stress and lead to pathogenesis of health problems, especially during neurodevelopment, in these infants (Al-Saleh et al, 2013).
    B) CASE REPORTS
    1) Mercury has been found in human milk of exposed and unexposed women at about the same concentration found in cord blood (Mattison et al, 1983).
    2) Gonzalez et al (1985) reported a significant correlation between total mercury concentrations measured in the hair of nursing neonates and the mercury levels determined in maternal samples.
    C) ANIMAL STUDIES
    1) GUINEA PIGS - Elemental mercury vapor at an airborne concentration of 6 to 9 mg/m(3) was transferred in the milk of guinea pigs to the offspring. Although speciation of the mercury present in the milk was not performed, tissue distribution made it likely that the mercury was inorganic rather than elemental (Yoshida et al, 1992).

Carcinogenicity

    3.21.1) IARC CATEGORY
    A) IARC Carcinogenicity Ratings for CAS7439-97-6 (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004):
    1) IARC Classification
    a) Listed as: Mercury and inorganic mercury compounds
    b) Carcinogen Rating: 3
    1) The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.
    3.21.2) SUMMARY/HUMAN
    A) Metallic mercury and inorganic mercury compounds are listed as Group 3 (not classifiable as to their carcinogenicity in humans) by the IARC CANCER REVIEW, based on inadequate evidence in humans for the carcinogenicity of mercury and mercury compounds, inadequate evidence in experimental animals for the carcinogenicity of metallic mercury, and limited evidence in experimental animals for the carcinogenicity of mercuric chloride (IARC, 1997).
    3.21.3) HUMAN STUDIES
    A) SUMMARY
    1) Mercury is classified as Group D (not classifiable as to human carcinogenicity) by IRIS, based on inadequate human and animal data ((IRIS, 2001)). It is listed with an A4 notation by the ACGIH, indicating it is not classifiable as a human carcinogen (ACGIH, 2000).
    B) CASE REPORTS
    1) A borderline excess of lung cancer incidence was reported in Norwegian chloralkali workers exposed to mercury (Ellingsen et al, 1993a). Exposure to inorganic mercury in mines and mills does not seem to be strongly associated with cancer risk, with the possible exception of liver cancer (Boffetta et al, 1998).
    3.21.4) ANIMAL STUDIES
    A) SUMMARY
    1) There is sufficient evidence in experimental animals for the carcinogenicity of methylmercury chloride; methylmercury compounds are classified as Group 2B (possibly carcinogenic to humans)(IARC, 1997).
    B) MICE
    1) Mercury at a dose of 5 ppm in the drinking water was not carcinogenic in mice (Schroeder & Mitchener, 1975). Mercury given intraperitoneally to rats produced tumors at the site of application ((RTECS, 2001)).
    2) Methylmercury chloride given in the diet produced renal tumors in male mice and no tumors in female mice. Mercuric chloride showed some evidence of carcinogenicity in male rats, but not in female mice; results in female rats and male mice were equivocal (Clayton & Clayton, 1994).

Genotoxicity

    A) SUMMARY of GENOTOXICITY/GENETIC EFFECTS -
    1) Results of cytogenetic monitoring of humans exposed to elemental mercury have primarily been negative (Mabille et al, 1984) or inconclusive (De Flora et al, 1994).
    2) Increased micronuclei, chromosome breaks and/or dicentrics among elemental mercury exposed persons have been reported (Hansteen et al, 1993; Verschaeve et al, 1976; Verschaeve et al, 1979). These effects were not statistically significant. Statistically significant increases in lymphocytic micronuclei have been reported by Queroz et al, (1999).
    3) Many studies involving humans have been limited by small sample size, combined exposures, or inability to quantitatively determine exposure.
    4) Animal models and in vitro studies have chiefly focused on other forms of mercury (De Flora et al, 1994). Mercuric ions and mercuric chloride have produced genotoxicity/genetic effects in some in vitro and in vivo studies (De Flora et al, 1994).

Monitoring Parameters Levels

    4.1.1) SUMMARY
    A) 24-hour urinary mercury concentration is the best marker for chronic exposure (patient should abstain from eating seafood for a week or the placement of mercury amalgams for several weeks prior to collection). Whole blood mercury concentration may be useful for acute exposure. Careful specimen collection is important to avoid contamination. A laboratory should use trace element collection tubes for blood samples and acid-washed containers for a 24-hour urine collection. Mercury levels of 10 mcg/L for whole blood and 20 mcg/L for urine typically reflect background exposure.
    B) Monitor serum electrolytes, renal function, glucose, urinalysis and liver enzymes in symptomatic patients.
    C) Monitor chest radiograph in patients with pulmonary symptoms.
    D) Specific urine markers for renal injury should include beta-2 microglobulin, microalbuminuria, and retinol binding protein in symptomatic patients.
    E) Postchelation mercury concentrations should not be utilized as the sole basis for the diagnosis of mercury poisoning and subsequent treatment. This is especially true if no baseline, prechelation concentration was measured.
    4.1.2) SERUM/BLOOD
    A) BLOOD/SERUM CHEMISTRY
    1) Blood level of mercury is a good indicator of recent exposure, as concentrations of mercury in whole blood rapidly rise after exposure (Barregard, 1993; Aks et al, 1995). The half-life for mercury in the blood is approximately 3 days (US DHHS, 1992).
    2) LIMITATIONS : Blood analysis is useful only for detecting acute exposure immediately after it has occurred. Blood mercury levels often do not correlate well with clinical signs of toxicity (Aks et al, 1995). Some analytical methods do not distinguish between inorganic and organic mercury in biological samples (Knight, 1988).
    3) NORMAL CONCENTRATIONS IN UNEXPOSED: Normal whole blood mercury levels rarely exceed 1.5 mcg/dL in unexposed adults (US DHHS, 1992).
    4) CONCENTRATIONS ASSOCIATED WITH SYMPTOMS: Symptoms of toxicity may occur in some individuals at blood mercury concentrations of 5 mcg/dL or greater. Many individuals with high blood mercury levels do not exhibit clinical symptoms.
    a) In acute situations, elevation of blood-mercury level to ranges of 25 to 50 mcg/dL (1246.2 to 2492.5 nmol/L) precede elevations in urinary excretion because of the body's capacity to store mercury (Cherian et al, 1978).
    5) SEAFOOD: The use of blood mercury levels after acute exposure should be considered with the knowledge that a single seafood meal will elevate levels for 20 to 30 hours (Kershaw et al, 1980; Sherlock et al, 1984).
    6) OTHER SERUM/BLOOD ASSAYS: The measurement of glomerular basement antibodies (alpha-GBMs) in serum is being studied as a biological indicator of chronic elemental mercury vapor exposure and effects (Ellingsen et al, 1993).
    4.1.3) URINE
    A) URINARY LEVELS
    1) URINARY MERCURY is the best biological marker for chronic elemental or inorganic mercury exposure.
    2) LIMITATIONS: Urinary mercury levels often do not correlate with clinical signs and symptoms of toxicity.
    3) NORMAL CONCENTRATIONS IN UNEXPOSED INDIVIDUALS: Normal urine excretion rarely exceeds 15 mcg/L (74.7 nmol/L) in unexposed individuals. There is a high degree of intraindividual variation in urine mercury levels. The averaging of several urinary mercury determinations may be required (Barregard, 1993).
    4) 24-HOUR URINE COLLECTION: A 24-hour urine specimen is preferred if chronic exposure to elemental mercury or mercury salts is suspected (US DHHS, 1992). Spot sample collecting can be used to approximate the 24-hour sample.
    a) Collection of a 24-hour urine sample, followed by challenge with D-penicillamine for 4 days, has been used to document mercury body burden (Ishihara et al, 1974).
    5) URINARY MERCURY FOLLOWING DENTAL PROCEDURE: Urinary concentrations of mercury were obtained in normal 5 to 7 year old children before and 9 to 12 days after dental work. Concentrations were 3.83 +/- 2.45 and 5.14 +/- 3.14 microg/L respectively (Khordi-Mood et al, 2001). Results did not correlate with age, sex, weight, or number of fillings placed.
    6) SPOT MERCURY LEVELS: Methods of collecting spot samples to closely approximate the 24-hour collection and to avoid contamination are described by Barregard (1993). A first morning void can be used to approximate a 24-hour urine collection.
    a) The interpretation of these levels is most accurate when samples are taken at the same time of day and are corrected for specific gravity or, more preferably, creatinine (US DHHS, 1992; Calder et al, 1984).
    b) Spot urine mercury levels correlated with the occurrence of neuropsychological toxicity and motor nerve conduction velocity effects in 42 chronically exposed workers (Rosenmann et al, 1986).
    c) Workers chronically exposed to mercury vapor exhibited preclinical renal toxicity at spot urine mercury levels of greater than 50 mcg/g creatinine (Roels et al, 1985).
    B) OTHER
    1) TOTAL MERCURY BODY BURDEN/CHELATION STUDIES: Chelation tests have been used to evaluate the body burden of mercury in individuals with non-specific symptoms who have dental amalgams in an attempt to confirm or refute mercury toxicity. In a small study (n=15), healthy volunteers were given a 30 mg/kg oral loading dose of dimercaptosuccinic acid (DMSA). Pre and post-DMSA urine samples were analyzed for mercury and creatinine. The findings were comparable with the mean concentrations found in previously reported studies with symptomatic subjects. One volunteer had an anaphylactoid response following DMSA administration.
    a) The results showed a correlation between predose urinary mercury : creatinine ratios, and both the total number of amalgam surfaces and the number of occlusal surfaces. The mean increase in the urinary Hg/Creatinine ration after chelation was 7.0 fold (+/- 6.4). Since the levels reported were similar to levels previously reported in subjects with symptoms attributed to "amalgam poisoning", the authors concluded that the use of oral DMSA as a diagnostic tool has limited validity in this setting, and further suggested that an oral DMSA chelation test may provide misleading evidence regarding mercury toxicity. In addition, DMSA can result in serious adverse effects (Archbold et al, 2004).
    2) Increased urinary excretion of mercury following chelation challenge should not be used as the sole basis for diagnosing mercury poisoning, particularly if further chelation treatment is to be considered (Risher & Amler, 2005).
    3) 24 HOUR URINARY DELTA AMINOLEVULINIC ACID (ALA) levels are invariably elevated to 3 to 10 mg/L in chronic poisoning cases. Although urinary levels as high as 2000 mcg/L have been seen without symptoms, behavioral and neurological evaluation should be performed if levels are greater than 100 mcg/L (Adams et al, 1983).
    4) TOTAL URINARY PROTEIN levels positively correlated with the level of blood and urinary mercury, and with the exposure duration (Abdelmegid et al, 1993). PROTEINURIA has been reported after acute and chronic mercury vapor exposure (Snodgrass et al, 1981) Rosenmann et al, 1986; Ehrenberg, 1991).
    5) URINARY PORPHYRIN PROFILES may reflect renal mercury content and the biological effects of mercury in the kidney. Significant differences in urinary porphyrin levels among mercury exposed dentists, as compared to unexposed dentists, have been reported (Woods et al, 1993). However, Frumkin et al, (2001) could not demonstrate a correlation of exposure with urinary porphyrins in chloralkali workers. Mean precoproporphyrin and coproporphyrin concentrations were 1.5 to 2-fold higher in urine samples from the mercury exposed dentist than from the unexposed dentists, after adjusting for urinary creatinine. Changes in urinary porphyrins correlated better with urinary mercury concentrations when adjustments for urinary creatinine were NOT made (Frumkin et al, 2001).
    6) ENZYMURIA is considered to represent renal tubule effects. N-acetyl beta-glucosaminidase (NAG) is a high molecular weight lysosomal enzyme that is a sensitive but nonspecific indicator of early renal injury. Elevations in urinary NAG levels have been associated with chronic low level mercury exposure (Rosenmann et al, 1986).
    a) The NAG isoenzymes A and G have also been used as early indicators of renal dysfunction (Ellingsen et al, 1993b; Ellingsen et al, 2000).
    7) URINARY INTESTINAL ALKALINE PHOSPHATASE (IAP) is a marker of effects on the S3 segment of the renal proximal tubule, a site of mercury effects. An enzyme-antigen immunoassay with specific monoclonal antibodies to IAP has been developed.
    a) One study found statistically significant increased release of IAP in the urine of chloralkali workers, compared to controls (Verpooten et al, 1992).
    4.1.4) OTHER
    A) OTHER
    1) HAIR
    a) Measurement of mercury in the hair can be used to identify exposure to methyl mercury compounds, but is not useful for monitoring exposure to elemental mercury (US DHHS, 1992; IARC, 1993).
    b) Analysis of hair segments can provide an estimation of the time and extent of methyl mercury exposure, with new growth reflecting the most current exposure status. Hair samples may be externally contaminated with mercury from the air. External mercury must be removed before analysis.
    c) In a study of 162 dentists' and their assistants' mercury levels in hair and urine, the dentists demonstrated higher levels (Herber et al, 1988).
    d) Maternal and neonatal hair samples were obtained from 82 subject pregnancies of which 27 had received maternal dental amalgams during gestation. Maternal and neonatal hair mercury concentrations were 0.39 (range 0.1-2.13) and 0.24 (range 0.1-1.93) micrograms per gram of hair respectively. Dental restoration was associated with a statistically higher level of maternal and neonatal hair mercury (Razagui & Haswell, 2001).
    2) ELECTROPHYSIOLOGICAL TESTING
    a) Nerve conduction velocity studies in workers chronically exposed to inorganic mercury are informative for evaluation of mercury toxicity. Slowing of the median motor nerve correlated with both increased blood and urine mercury levels and an increased number of neurologic symptoms (Singer et al, 1987).
    b) TREMOR ANALYSIS: Clinically apparent tremors often occur with chronic mercury poisoning (Knight, 1988).
    1) One study described methods of measuring tremor frequency and other tremor characteristics which may enable identification of subtle neurological effects before clinical signs of poisoning are evident (Chapman et al, 1990).
    2) The reliability of tremor measurement has been examined in detail (Letz & Gerr, 2000).
    3) SALIVA
    a) Saliva concentrations have been measured in individuals with dental amalgam fillings. Saliva concentration appears to be related to the number of fillings present and to the surface area of amalgam exposed (Pizzichini et al, 2000).
    b) However, saliva values correlated only weakly with serum or urinary mercury excretion, and salivary levels did not appear to be appropriate measures of mercury burden related to dental amalgam (Ganss et al, 2000).
    4) CEREBROSPINAL FLUID
    a) CEREBROSPINAL FLUID (CSF) was assayed for mercury in 10 subjects occupationally exposed to mercury vapors and 16 unexposed controls (Sallsten et al, 1994). The CSF mercury concentrations were very low, but correlated with plasma concentrations of mercury.
    b) The plasma concentrations of mercury appeared to provide a better indication of exposure than CSF mercury. CSF mercury decreased in two individuals shortly after they ceased mercury exposure, possibly indicating that the mercury pool in the brain has a rapid turnover.
    5) MONITORING
    a) If respiratory tract irritation is present, monitor arterial blood gases and chest x-ray.
    b) If respiratory tract irritation is present, it may be useful to monitor pulmonary function tests.
    6) NEUROPSYCHOLOGICAL TESTING
    a) Two studies reported the use of tests to identify subtle psychological and neurological effects of elemental mercury. The tests included the Questionnaire 16 survey of symptoms, the Eysenck Personality Inventory, the Profile of Mood State, and the Chinese version Neurobehavioral Evaluation System which measures domains of intelligence, memory, visual perception, and psychomotor skills (Liang et al, 1993; Langworth et al, 1992).
    b) Yeates & Mortensen (1994) described the use of an extensive battery of tests to monitor neuropsychological effects of mercury vapor exposure in 2 adolescents. Vocabulary, verbal repetition, memory skills, visual-motor abilities, sensory/motor function, sorting, and categorization skills were assessed through these tests (Yeates & Mortensen, 1994).
    c) Soleo et al (1990) described the use of the Gordon Personal Profile, Simple Reaction Time test, Benton Visual Recognition test, Santa Ana Dexterity test, Wechsler Adult Intelligence Scale, and the Clinical Depression Questionnaire to evaluate workers at a fluorescent lamp factory (Soleo et al, 1990). These tests, excluding the Gordon Personal Profile, are part of the WHO test battery to detect preclinical signs of neurological impairment.

Radiographic Studies

    A) CHEST RADIOGRAPH
    1) If respiratory tract irritation is present, monitor chest x-ray.
    2) INTRAVENOUS INJECTION: Intravenously injected metallic mercury is generally visible on chest radiograph as multiple metallic densities scattered throughout both lung fields. Chelation therapy does not significantly reduce the quantity of embolized mercury.
    3) CASE REPORT: A 40-year-old man developed dyspnea, fever, tachycardia, and mild gastrointestinal disturbances after the intravenous injection of 3 mL of elemental mercury and ingestion of 3 mL in a suicide attempt. Chest X-ray showed scattered pulmonary infiltrates and embolized mercury bilaterally. Following chelation therapy, his pulmonary and renal functions improved over the next 36 hours (McFee & Caraccio, 2001).
    B) ABDOMINAL RADIOGRAPH
    1) Liquid mercury released in the gastrointestinal tract will generally pass through without producing toxicity. Occasionally, the mercury may get hung up in the intestine and may require surgical removal (Cantor, 1951).
    a) Even in patients without a fistula, mercury may remain in the appendix, producing inflammation (Birnbaum, 1947; Sawyer, 1967) and rupture (Crikelair & Hiratzka, 1953).
    2) An x-ray should be obtained several days postingestion to document passage of the mercury IF:
    1) the patient has a history of known decreased GI transit or fistula
    2) the patient has a history of inflammatory bowel disease
    3) a large amount of mercury is ingested (greater than that contained in a household thermometer).
    3) Obtain chest x-ray if aspiration of mercury is suspected (symptoms of cough, fever, dyspnea).
    4) CASE REPORT: A 34-year-old man presented with fever, vomiting, and hemoptysis 2 days after the self-injection of 25 mL of elemental mercury in a suicide attempt. On presentation, his plasma mercury concentration was 2625 mcg/L (upper limit of exposure: 15 mcg/L). A chest x-ray revealed several metallic densities throughout both lung fields, with numerous mercury deposits in the pulmonary venous circulation, and in the right auricular and ventricular cavities. An abdominal x-ray revealed mercury embolism of renal arteries. Following the excision of all affected subcutaneous tissues, he received dimercaptosuccinic acid (10 mg/kg 3 times daily for 15 days); however, his blood mercury concentration did not decrease significantly. His serum creatinine concentrations were between 70 to 80 mcmol/L during the first month and it increased to 164 mcmol/L 2 years post-exposure. Within the next 3 years, he developed recurrent subcutaneous abscess with droplets of mercury, sensory motor polyneuropathy, and a toxic megacolon complicated by peritonitis. He was started on hemodialysis 4 years after exposure and remains to be hemodialysis dependent 12 years after exposure (Truche et al, 2012).
    C) RADIOGRAPHIC-OTHER
    1) A 3-year-old girl who had swallowed mercury from a broken thermometer experienced no apparent adverse effects (Martijn et al, 1990). Mercury droplets were identified by abdominal x-ray.
    a) Oral laxatives and a laxative diet were provided, with follow-up radiographic studies to insure passage of the mercury. No symptomology and no increased mercury levels in the blood or urine were detected 6 weeks after the ingestion.
    2) Rectal perforation from a broken thermometer resulted in systemic mercury absorption in a 10-month-old child (Maurage et al, 1989).
    D) MRI
    1) A 10-year-old boy developed acrodynia, seizures and visual impairment after exposure to elemental mercury for 20 days. A brain MRI revealed multiple supratentorial hyperintense lesions on T2-weighted images ranging in size from 1 cm to 3 cm in maximum diameter, with lesions located in the cerebral white matter in paracentral gyrus, and left globus pallidus and putamen. Following chelation therapy, he recovered completely and the lesions in the brain MRI resolved (Abbaslou & Zaman, 2006).
    E) COMPUTED TOMOGRAPHY (CT)
    1) In one study, 6 of 8 men (37 to 54 years; mean, 49 years) exposed to mercury vapor while cutting pipes in a sulfuric acid plant had abnormal chest CT results, with alveolar consolidation in 3 patients and areas of ground-glass opacity (mainly subpleural and upper lungs) in 4 patients. Two of the 6 patients were asymptomatic. Five of the 6 patients with positive CT findings had poorly defined nodules, that were centrilobular. All 6 patients recovered following medical treatment. Pathological findings in the most severely affected patient revealed ground-glass opacity and consolidation corresponded to an acute interstitial pneumonitis. All abnormal findings resolved on follow-up CT in all patients (Hashimoto et al, 2001).

Methods

    A) MULTIPLE ANALYTICAL METHODS
    1) Blood, urine, hair, and nails can be analyzed for mercury content.
    2) The most reliable and commonly used method for blood mercury analysis is cold vapor atomic absorption.
    3) The neutron activation procedure for urinary mercury analysis is reported by the WHO as the most accurate and sensitive method (IARC, 1993). Cold vapor atomic absorption is also commonly used.
    4) Single hair strands can be analyzed by x-ray fluorescence (XRF) spectrometry without destroying the hair sample (Toribara et al, 1982). An average rate of uniform hair growth is 1.1 cm/month (Shahristani & Shihab, 1974).
    a) A procedure for determination of mercury in hair by cold vapor atomic absorption spectrometry with a new reaction vessel is suited for use with a large number of samples (Pineau et al, 1990).
    5) A method for the determination of toxic quantities of mercury was reported in simulated stomach contents by energy dispersive x-ray fluorescence (EDXRF).
    a) The lower limit of detection was 10 mcg/mL in simulated stomach contents (soup) (Winstanley et al, 1987). This method may not detect mercury at quantities near a normal value.
    6) One study described a cold vapor atomic fluorescence spectrometric method which can detect very low levels of total mercury in biological samples, and which can be adapted in order to differentiate between inorganic and organic mercury (Winfield et al, 1994).
    a) Atomic absorption, gas chromatography, and reverse-phase high-performance liquid chromatography, are other methods which can be used to speciate the type of mercury in biological samples (IARC, 1993; Sallsten et al, 1994; Aks et al, 1995).
    b) Other analytical methods typically used to quantitate mercury in biological tissues include neutron activation analysis, inductively coupled plasma emission spectrometry, and spark source spectrometry (IARC, 1993).
    c) Simultaneous determination of inorganic, monomethyl, and total mercury can be accomplished in biological samples by digestion in methanolic potassium hydroxide, followed by ethylation and gas chromatography with cold vapor atomic fluorescence spectrometry (CVAFS). Limits of detection are 1.3 pg inorganic mercury and 0.6 pg monomethyl mercury (Liang et al, 1994).

Life Support

    A) Support respiratory and cardiovascular function.

Patient Disposition

    6.3.1) DISPOSITION/ORAL EXPOSURE
    6.3.1.1) ADMISSION CRITERIA/ORAL
    A) Any symptomatic patient (dyspnea, hypoxia, wheezes, gastrointestinal complaints) should be admitted to the intensive care unit. Patients with chronic exposure should be removed from exposure and chelated if symptomatic; this may require admission.
    6.3.1.2) HOME CRITERIA/ORAL
    A) (Caravati et al, 2008).
    1) Asymptomatic patients with brief, , low-dose vapor exposures, tract may be observed at home. Patients with unintentional ingestion of less than the amount of mercury in a fever thermometer who do not have abdominal pain can be observed at home. They may be referred to their physician at a convenient time for an x-ray to document the mercury's course after ingestion. If a small mercury spill has been vacuumed or swept the health department should be notified to perform environmental monitoring and the patient referred for evaluation if ambient concentrations are high.
    6.3.1.3) CONSULT CRITERIA/ORAL
    A) Consult a toxicologist for assistance in managing patients with mercury toxicity.
    6.3.1.5) OBSERVATION CRITERIA/ORAL
    A) The following patients should be referred to a healthcare facility for observation and treatment: patients with suspected self-harm, abuse, or malicious use of elemental mercury; patients with symptoms of acute (eg, cough, dyspnea, chest pain) or chronic (eg, rash, tremor, weight loss) exposure to elemental mercury; exposure to recently heated (eg, stove top, oven, furnace) elemental mercury; patients exposed to documented high air mercury concentrations; patients who ingested more mercury than in a household fever thermometer or those with abdominal pain after ingestion; patients with elemental mercury deposited or injected into soft tissue. Observe patients with inhalation exposure for 6 to 12 hours for respiratory disease progression. The results of blood and urine mercury concentrations (usually require an outside laboratory analysis) will not influence acute care. (Caravati et al, 2008).

Monitoring

    A) 24-hour urinary mercury concentration is the best marker for chronic exposure (patient should abstain from eating seafood for a week or the placement of mercury amalgams for several weeks prior to collection). Whole blood mercury concentration may be useful for acute exposure. Careful specimen collection is important to avoid contamination. A laboratory should use trace element collection tubes for blood samples and acid-washed containers for a 24-hour urine collection. Mercury levels of 10 mcg/L for whole blood and 20 mcg/L for urine typically reflect background exposure.
    B) Monitor serum electrolytes, renal function, glucose, urinalysis and liver enzymes in symptomatic patients.
    C) Monitor chest radiograph in patients with pulmonary symptoms.
    D) Specific urine markers for renal injury should include beta-2 microglobulin, microalbuminuria, and retinol binding protein in symptomatic patients.
    E) Postchelation mercury concentrations should not be utilized as the sole basis for the diagnosis of mercury poisoning and subsequent treatment. This is especially true if no baseline, prechelation concentration was measured.

Oral Exposure

    6.5.1) PREVENTION OF ABSORPTION/PREHOSPITAL
    A) SUMMARY
    1) ELEMENTAL (METALLIC) MERCURY - is usually not absorbed, and usually does not produce acute toxicity unless a GI fistula or another inflammatory process is present or the mercury is retained for a long period in the GI tract. Decontamination is not necessary in normal patients after small ingestions.
    6.5.2) PREVENTION OF ABSORPTION
    A) SUMMARY
    1) Whole bowel irrigation may assist in cases of large volume ingestion, prolonged retention, mucosal inflammation, or fistula. Surgical removal is almost never needed.
    2) Liquid mercury released in the gastrointestinal tract will generally pass through without producing toxicity. An x-ray should probably be obtained to document its course. Elemental mercury will appear round, with a diameter of less than 1 mm to 3 mm (Martijn et al, 1990). These droplets may become smaller as they progress through the intestinal tract. Dental amalgam mercury is irregular in shape.
    B) ACTIVATED CHARCOAL
    1) While activated charcoal is known to adsorb mercuric chloride, it is not known if it adsorbs elemental mercury. Activated charcoal and laxatives have been used in some cases of retained elemental mercury in the gastrointestinal tract (McKinney, 1999; Martijn et al, 1990).
    C) WHOLE BOWEL IRRIGATION
    1) Consider in patients at risk for poisoning after ingestion of elemental mercury (large ingestion, prolonged retention, inflammation of the GI mucosa, known fistula etc). Consider whole bowel irrigation in these cases.
    a) WHOLE BOWEL IRRIGATION/INDICATIONS: Whole bowel irrigation with a polyethylene glycol balanced electrolyte solution appears to be a safe means of gastrointestinal decontamination. It is particularly useful when sustained release or enteric coated formulations, substances not adsorbed by activated charcoal, or substances known to form concretions or bezoars are involved in the overdose.
    1) Volunteer studies have shown significant decreases in the bioavailability of ingested drugs after whole bowel irrigation (Tenenbein et al, 1987; Kirshenbaum et al, 1989; Smith et al, 1991). There are no controlled clinical trials evaluating the efficacy of whole bowel irrigation in overdose.
    b) CONTRAINDICATIONS: This procedure should not be used in patients who are currently or are at risk for rapidly becoming obtunded, comatose, or seizing until the airway is secured by endotracheal intubation. Whole bowel irrigation should not be used in patients with bowel obstruction, bowel perforation, megacolon, ileus, uncontrolled vomiting, significant gastrointestinal bleeding, hemodynamic instability or inability to protect the airway (Tenenbein et al, 1987).
    c) ADMINISTRATION: Polyethylene glycol balanced electrolyte solution (e.g. Colyte(R), Golytely(R)) is taken orally or by nasogastric tube. The patient should be seated and/or the head of the bed elevated to at least a 45 degree angle (Tenenbein et al, 1987). Optimum dose not established. ADULT: 2 liters initially followed by 1.5 to 2 liters per hour. CHILDREN 6 to 12 years: 1000 milliliters/hour. CHILDREN 9 months to 6 years: 500 milliliters/hour. Continue until rectal effluent is clear and there is no radiographic evidence of toxin in the gastrointestinal tract.
    d) ADVERSE EFFECTS: Include nausea, vomiting, abdominal cramping, and bloating. Fluid and electrolyte status should be monitored, although severe fluid and electrolyte abnormalities have not been reported, minor electrolyte abnormalities may develop. Prolonged periods of irrigation may produce a mild metabolic acidosis. Patients with compromised airway protection are at risk for aspiration.
    D) SURGICAL THERAPY
    1) Rarely, mercury may get hung up in the intestine and may require surgical removal (Cantor, 1951).
    6.5.3) TREATMENT
    A) SUPPORT
    1) INGESTION: Ingestion usually does not result in acute toxicity since elemental mercury is poorly absorbed. Obtain an x-ray to document its presence and course. Whole bowel irrigation may assist in cases of large volume ingestion, prolonged retention, mucosal inflammation, or fistula. Surgical removal is almost never needed. Postural drainage or suctioning may aid in the removal of aspirated elemental mercury.
    2) INHALATION: Inhalation is the prime source of significant toxicity, especially after vaporization from heating or vacuuming spills. Ventilate the area for 15 minutes and pick up mercury globules with cardboard or duct tape. If vacuuming is required, discard the bag in 2 sealed plastic bags immediately after use. Thermometers contain about 500 mg of mercury and can cause significant injury if vaporized by vacuuming. Move the patient to fresh air. Monitor for respiratory distress and hypoxia. Give 100% humidified oxygen, intubate, and assist ventilation as needed. Administer beta-2 adrenergic agonists for bronchospasm. Severe pulmonary toxicity may mandate admission to an intensive care unit for meticulous supportive care and respiratory management.
    3) INTRAVENOUS or INTRAMUSCULAR: IV or IM injection usually requires only supportive care.
    4) DIFFERENTIAL DIAGNOSIS: Pheochromocytoma; Kawasaki's disease; brucellosis; Creutzfeldt-Jakob disease (Tang et al, 2015; Sasan et al, 2012).
    B) MONITORING OF PATIENT
    1) 24-hour urinary mercury concentration is the best marker for chronic exposure (a patient should abstain from eating seafood for a week or the placement of mercury amalgams for several weeks prior to collection). Whole blood mercury concentration may be useful for acute exposure. Specimen collection method is important to avoid contamination. A laboratory should use trace element collection tubes for blood samples and acid-washed containers for a 24-hour urine collection. Mercury levels of 10 mcg/L for whole blood and 20 mcg/L for urine typically reflect background exposure.
    2) Monitor serum electrolytes, renal function, glucose, urinalysis and liver enzymes in symptomatic patients.
    3) Monitor chest radiograph in patients with pulmonary symptoms.
    4) Specific urine markers for renal injury should include beta-2 microglobulin, microalbuminuria, and retinol binding protein in symptomatic patients.
    5) Postchelation mercury levels should not be utilized as the sole basis for the diagnosis of mercury poisoning and subsequent treatment. This is especially true if no baseline, prechelation concentration was measured.
    C) SURGICAL PROCEDURE
    1) Intraoperative removal of ingested elemental mercury is usually unnecessary and presents risks. Appendiceal mercury without signs of appendicitis is NOT an indication for intraoperative mercury removal. Peritoneal spillage of mercury may result as a risk of operative procedures.
    a) McVittie & Berlin (1998) reported an operative intervention in the case of a massive mercury ingestion (60 mL) along with the development of appendiceal mercury. Following an appendectomy and suctioning of the colon, mercury spillage into the peritoneal cavity resulted. The patient subsequently developed elevated blood and urinary mercury concentrations and signs and symptoms of mercury poisoning (tremor, insomnia, forgetfulness, ataxia).

Inhalation Exposure

    6.7.1) DECONTAMINATION
    A) Move patient from the toxic environment to fresh air. Monitor for respiratory distress. If cough or difficulty in breathing develops, evaluate for hypoxia, respiratory tract irritation, bronchitis, or pneumonitis.
    B) OBSERVATION: Carefully observe patients with inhalation exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
    C) INITIAL TREATMENT: Administer 100% humidified supplemental oxygen, perform endotracheal intubation and provide assisted ventilation as required. Administer inhaled beta-2 adrenergic agonists, if bronchospasm develops. Consider systemic corticosteroids in patients with significant bronchospasm (National Heart,Lung,and Blood Institute, 2007). Exposed skin and eyes should be flushed with copious amounts of water.
    D) Chelation therapy may be necessary in patients with prolonged or severe exposure.
    6.7.2) TREATMENT
    A) SUPPORT
    1) Acute inhalation exposure to mercury vapor can produce local effects on the pulmonary system as well as systemic toxicity and elevated urine and blood mercury concentrations (Levin et al, 1988). Chelation may be required.
    2) ACRODYNIA: Nifedipine 0.2 mg/kg four times daily initially, increasing to 0.2 mg/kg six times daily while monitoring blood pressure has been used to alleviate the pinkish skin color, extremity pain, anorexia, and proteinuria seen with acrodynia resulting from mercury poisoning (Ozsoylu, 1993).
    a) A topical mixture of mexiletine 2%, a lidocaine analog, and ketamine 2% provided transient pain control in hands and feet of a 3-year-old girl with acrodynia secondary to toxic exposure to elemental mercury (Mercer et al, 2012).
    3) PAIN MANAGEMENT: Severe neuropathic pain has been treated with a combination of carbamazepine (20 mg/kg per day) and pyridoxine (300 mg/day) (Karagol et al, 1998). The mechanism of pain relief of carbamazepine, a sodium-dependent channel blocker, appears to be longer-lasting decrease of repetitive discharges, increase of firing threshold and decreased hyperexcitability.
    a) Three children with mercury poisoning received gabapentin (300 mg to 1800 mg daily in divided doses for 5 to 10 months) and tramadol (100 mg daily in divided doses) for peripheral neuropathic pain. Their symptoms gradually improved (Celebi et al, 2008).
    B) CHELATION THERAPY
    1) SUMMARY
    a) Chelation therapy has been used in treating persons with toxicity secondary to acute or chronic inhalation of elemental mercury vapors. Chelation should be performed with one of the following drugs in severe poisonings.
    b) In general, parenteral chelation therapy should be initiated in patients with significant acute exposures (acute inhalation with pulmonary, GI or neurologic effects). Either intramuscular dimercaprol (BAL) or intravenous unithiol can be used, depending on availability. When the patient is improving and able to tolerate oral medications, BAL can be replaced with succimer with no waiting period between treatments. If unithiol is used, therapy may be changed to the oral route after the fifth day if the patient's condition permits.
    c) All of the effective complexing agents administered to facilitate removal of mercury from the body contain sulfhydryl groups (Clarkson, 1990). However, clear clinical data showing improved clinical outcomes in lacking (Risher & Amler, 2005).
    C) SUCCIMER
    1) EFFICACY
    a) SUMMARY: 2,3-Dimercaptosuccinic acid (DMSA; succimer) is an effective mercury chelator with minimal side effects (Clarkson, 1990; Graziano, 1986; Graziano et al, 1978; Graziano et al, 1985; Kosnett et al, 1989).
    1) It is currently approved only for the treatment of childhood lead poisoning.
    2) Urinary excretion of mercury was enhanced by administration of oral DMSA in doses of 300 to 400 mg/day (Campbell et al, 1986), 30 mg/kg/day for 5 days (Fournier et al, 1988), and 2 grams as a single dose (Roels et al, 1991).
    b) CASE SERIES: Bluhm et al (1992) reported DMSA is superior to N-acetyl penicillamine (NAP) based on the ability of DMSA to induce a 3-fold increase in mercury excretion compared with a 2-fold increase with NAP and fewer adverse drug reactions noted with DMSA in a study of 23 patients exposed to elemental mercury vapor during an industrial accident.
    c) CASE REPORT: In a case of elemental mercury absorption in the small bowel of a 64-year-old cancer patient, a treatment regimen of 10 mg/kg every 8 hours for 9 days, 4 days without chelation therapy, and 7 mg/kg every 8 hours for an additional 23 days resulted in mean 24 hour urines of 1,127, 824, and 1,500 mcg/gram creatinine, respectively, for the three treatment periods (Kosnett et al, 1989).
    d) CASE SERIES: Oral succimer (dosage not specified) was effective in the treatment of 10 family members exposed to high air concentrations of mercury after home elemental mercury contamination (Boyer Hassen et al, 1992).
    e) CASE SERIES: Urinary mercury increased 1.2 to 6.1 times during succimer chelation in 6 patients with elemental mercury poisoning. Two patients were treated with a single course of succimer (30 mg/kg/d for 5 days followed by 20 mg/kg/d for 14 days). The other four patients received two courses of therapy each (Eti et al, 1992).
    f) CASE REPORT: Chronic intermittent therapy with 10 mg/kg every 8 to 12 hours for one week alternated with 2-weeks between courses was given for 2 years in an adult male who injected 10 mL intravenously. After 2 years, the lung mercury area decreased by 73% and renal function was normal (Winter et al, 1992).
    2) SUCCIMER/DOSE/ADMINISTRATION
    a) PEDIATRIC: Initial dose is 10 mg/kg or 350 mg/m(2) orally every 8 hours for 5 days (Prod Info CHEMET(R) oral capsules, 2011).
    1) The dosing interval is then increased to every 12 hours for the next 14 days. A repeat course may be given if indicated by elevated blood levels. A minimum of 2 weeks between courses is recommended, unless blood lead concentrations indicate the need for prompt retreatment.
    2) Succimer capsule contents may be administered mixed in a small amount of food (Prod Info CHEMET(R) oral capsules, 2011).
    b) ADULT: Succimer is not FDA approved for use in adults, however it has been shown to be safe and effective when used to treat adults with poisoning from a variety of heavy metals (Fournier et al, 1988). Initial dose is 10 mg/kg or 350 mg/m(2) orally every 8 hours for 5 days (Prod Info CHEMET(R) oral capsules, 2011).
    1) The dosing interval then is increased to every 12 hours for the next 14 days. A repeat course may be given if indicated by elevated blood levels. A minimum of 2 weeks between courses is recommended, unless the patient's symptoms or blood concentrations indicate a need for more prompt treatment (Prod Info CHEMET(R) oral capsules, 2011).
    3) MONITORING PARAMETERS
    a) The manufacturer recommends monitoring liver enzymes and complete blood count with differential and platelet count prior to the start of therapy and at least weekly during therapy (Prod Info CHEMET(R) oral capsules, 2011).
    b) Succimer therapy did not worsen preexisting borderline abnormal liver enzyme levels in a prospective evaluation of 15 children with lead poisoning (Kuntzelman & Angle, 1992).
    4) SUCCIMER/ADVERSE EFFECTS: The following adverse events have occurred in children and adults during clinical trials: nausea, vomiting and diarrhea; transient liver enzyme elevations; rash, pruritus; drowsiness and paresthesia. Events reported infrequently include: sore throat, rhinorrhea, mucosal vesicular eruption, thrombocytosis, eosinophilia, and mild to moderate neutropenia (Prod Info CHEMET(R) oral capsules, 2011).
    5) ODOR: Succimer has a sulfurous odor that may be evident in the patient's breath or urine (Prod Info CHEMET(R) oral capsules, 2005).
    6) HYPERTHERMIA: One adult developed acute severe hyperthermia associated with hypotension; rechallenge resulted in hyperthermia with shaking chills and hypertension (Marcus et al, 1991).
    7) AVAILABLE FORMS: Succimer (Chemet (R)), 100 mg capsules (Prod Info CHEMET(R) oral capsules, 2011).
    D) PENICILLAMINE
    1) D-penicillamine has been shown to increase urinary mercury excretion in patients with acute and chronic poisoning from elemental mercury (Snodgrass et al, 1981; Yang et al, 1994; Ambre et al, 1977).
    2) USUAL ADULT DOSE
    a) 1 to 1.5 g/day given orally in 4 divided doses (Nelson, 2011).
    3) USUAL PEDIATRIC DOSE
    a) 15 to 30 mg/kg/day in 3 to 4 divided doses. Initially, a small dose may be given to minimize side effects and then increased gradually (eg, 25% of the desired dose in week 1, 50% in week 2, and the full dose by week 3) (Caravati, 2004; Prod Info DEPEN(R) titratable oral tablets, 2009).
    4) ADVERSE REACTIONS
    a) COMMON SIDE EFFECTS/CHRONIC DOSING: Fever, anorexia, nausea, vomiting, diarrhea, abdominal pain, proteinuria, and myalgia(Prod Info DEPEN(R) titratable oral tablets, 2009).
    1) SERIOUS ADVERSE EFFECTS: Nephrotic syndrome, hypersensitivity reactions, leukopenia, thrombocytopenia, aplastic anemia, agranulocytosis, cholestatic hepatitis, and various autoimmune responses (Prod Info DEPEN(R) titratable oral tablets, 2009; Feehally et al, 1987; Kay, 1986).
    5) DURATION OF THERAPY
    a) Administer D-penicillamine for 3 to 10 days with meticulous daily monitoring of urinary excretion of mercury. If urine mercury falls rapidly, body burden is probably small. Wait 10 days and repeat after a baseline collection to determine if there is a rise on re-chelation therapy indicating further body burden.
    b) Repeated courses of D-penicillamine may be required. Regular follow-up of blood and urine mercury levels will establish need for treatment.
    6) CAUTIONS
    a) Patients allergic to penicillin products may have cross-sensitivity to penicillamine (Prod Info DEPEN(R) titratable oral tablets, 2009).
    b) Monitor for proteinuria and hematuria; heavy metals may also cause renal toxicity (Prod Info DEPEN(R) titratable oral tablets, 2009).
    c) Monitor CBC with differential, platelet count, and hepatic enzymes (Prod Info DEPEN(R) titratable oral tablets, 2009).
    d) Renal failure makes therapy with D-penicillamine dangerous since the main route of elimination of this complex is renal.
    e) CROSS-REACTIVITY - The use of penicillamine in a patient with penicillin allergy is controversial.
    1) While positive penicillamine skin tests have been reported in 2.5 to 10% of patients with history of penicillin allergy, the risk of rash or anaphylaxis in these patients is unknown. One such patient did not react when challenged with oral penicillamine (Bell & Graziano, 1983).
    7) PREGNANCY
    a) Penicillamine is considered FDA pregnancy category D(Prod Info CUPRIMINE(R) oral capsules, 2004); it should be avoided if possible in pregnant patients.
    b) Use of penicillamine throughout pregnancy has been associated with connective tissue abnormalities, hydrocephalus, cerebral palsy, cardiac and great vessel anomalies, webbing of fingers and toes, and arthrogryposis multipex (Linares et al, 1979; Solomon et al, 1977; Anon, 1981; Beck et al, 1981; Rosa, 1986). However, the teratogenic effect when used in low doses or for short periods of time, as in metal chelation, has yet to be determined.
    E) N-ACETYL-PENICILLAMINE
    1) DOSE: Oral N-acetyl penicillamine (NAP) 250 mg to 500 mg, 4 times a day for 6 to 10 days (30 mg/kg/day in children) has been associated with increased urinary mercury excretion and clinical improvement in patients with toxicity from exposure to elemental mercury (Kark et al, 1971; Hryhorczuk et al, 1982; Gledhill & Hopkins, 1972). NAP is still considered experimental.
    F) DIMERCAPROL
    1) DIMERCAPROL/BAL IN OIL: INDICATIONS: Used for the treatment of mercury (inorganic and elemental), arsenic, and gold poisoning. It is also used in combination with Edetate Calcium Disodium injection to treat patients with severe lead poisoning (Prod Info BAL In Oil intramuscular injection, 2008). Dimercaprol is contraindicated in methyl mercury poisoning (Howland, 2002; Clarkson, 1990).
    2) MILD ARSENIC OR GOLD POISONING: DOSE: 2.5 mg/kg 4 times daily for 2 days, 2 times on the third day, and once daily thereafter for 10 days. SEVERE ARSENIC OR GOLD POISONING: DOSE: 3 mg/kg every 4 hours for 2 days, 4 times on the third day, then twice daily thereafter for 10 days. Administered by deep intramuscular injection only (Prod Info BAL In Oil intramuscular injection, 2008).
    3) MERCURY POISONING: DOSE: 5 mg/kg initially, then 2.5 mg/kg 1 or 2 times daily for 10 days. Administered by deep intramuscular injection only (Prod Info BAL In Oil intramuscular injection, 2008).
    4) ACUTE LEAD ENCEPHALOPATHY: DOSE: 4 mg/kg is given alone in the first dose and thereafter at 4-hour intervals with Edetate Calcium Disodium injection administered at a separate site. For less severe poisoning, dimercaprol dose can be decreased to 3 mg/kg after the first dose. Administered by deep intramuscular injection only. Continue the treatment for 2 to 7 days depending on clinical response (Prod Info BAL In Oil intramuscular injection, 2008). Therapy is generally switched to a less toxic oral chelator as soon as tolerated.
    5) ADVERSE EFFECTS: Common effects include pain at the injection site and fever (especially in children). Other effects include hypertension, tachycardia, nausea, vomiting, headache, burning sensations of the mouth and throat, a sensation of constriction in the throat, chest, or hands, conjunctivitis, lacrimation, salivation, tingling of the extremities, diaphoresis, abdominal pain, and anxiety. Dimercaprol injection contains peanut oil. Avoid in patients with peanut allergy (Prod Info BAL In Oil intramuscular injection, 2008). Adverse effects are dose related; they develop in 1% of patients receiving 2.5 mg/kg every 4 to 6 hours, 14% of patients receiving 4 mg/kg every 4 to 6 hours and 65% of patients receiving 5 mg/kg every 4 to 6 hours (Eagle & Magnuson, 1946).
    6) PRECAUTIONS: It is generally contraindicated in patients with hepatic insufficiency, with the exception of postarsenical jaundice (Prod Info BAL In Oil intramuscular injection, 2008). May cause hemolysis in G6PD deficient patients. BAL metal chelate disassociates in acid environment; urinary alkalinization is usually recommended. Do not administer with iron therapy as BAL iron complex may cause vomiting (Howland, 2002).
    7) LABORATORY: Monitor urine mercury excretion during chelation therapy to assess the effects of therapy.
    8) EFFICACY: Dimercaprol therapy was associated with increased urinary mercury excretion and decreased blood mercury levels in a 25-year-old male who injected elemental mercury intravenously (Murray & Hedgepeth, 1988).
    a) BAL increased urinary mercury excretion in 2 patients with acute poisoning from inhaling mercury fumes (Snodgrass et al, 1981).
    9) RENAL FAILURE
    a) BAL: therapy may be judiciously continued despite renal failure since a major fraction of this complex is excreted in bile and the complex can be dialyzed.
    G) UNITHIOL
    1) DMPS/INDICATIONS: Chelating agent for heavy metal toxicities associated with arsenic, bismuth, copper, lead and mercury (Blanusa et al, 2005).
    2) DMPS/DOSING
    a) ACUTE TOXICITY
    1) ADULT ORAL DOSE:
    a) 1200 to 2400 mg/day in equally divided doses (100 to 200 mg 12 times daily) (Prod Info DIMAVAL(R) oral capsules, 2004).
    2) ADULT INTRAVENOUS DOSE (Arbeitsgruppe BGVV, 1996; Prod Info Dimaval(R) intravenous intramuscular injection solution, 2013):
    a) If oral DMPS therapy is not feasible or in severe toxicity, it may be given intravenously.
    b) ADMINISTRATION: DMPS should be injected immediately after breaking open the ampule and should not be mixed with other solutions. DMPS should be injected slowly over 3 to 5 minutes. The opened ampules cannot be reused.
    c) First 24 hours: 250 mg intravenously every 3 to 4 hours (1500 to 2000 mg total).
    d) Day two: 250 mg intravenously every 4 to 6 hours (1000 to 1500 mg total).
    e) Day three: 250 mg intravenously every 6 to 8 hours (750 to 1000 mg total).
    f) Day four: 250 mg intravenously every 8 to 12 hours (500 to 750 mg total).
    g) Subsequent days: 250 mg intravenously every 8 to 24 hours (250 to 750 mg total).
    h) Depending on the patient's clinical status, therapy may be changed to the oral route.
    3) PEDIATRIC ORAL DOSE (Arbeitsgruppe BGVV, 1996; Blanusa et al, 2005):
    a) There are insufficient clinical data regarding the pediatric use of DMPS. It should be used only if medically necessary.
    b) Initial dose: 20 to 30 mg/kg/day orally in many equal divided doses.
    c) Maintenance dose: 1.5 to 15 mg/kg/day.
    4) PEDIATRIC INTRAVENOUS DOSE (Arbeitsgruppe BGVV, 1996; Blanusa et al, 2005; Prod Info Dimaval(R) intravenous intramuscular injection solution, 2013):
    a) There are insufficient clinical data regarding the pediatric use of DMPS. It should be used only if medically necessary.
    b) If oral DMPS therapy is not feasible or in severe toxicity, it may be given intravenously.
    c) ADMINISTRATION: DMPS should be injected immediately after breaking open the ampule and should not be mixed with other solutions. DMPS should be injected slowly over 3 to 5 minutes. The opened ampules cannot be reused.
    d) First 24 hours: 5 mg/kg intravenously every four hours (total 30 mg/kg).
    e) Day two: 5 mg/kg intravenously every six hours (total 20 mg/kg).
    f) Days three and four: 5 mg/kg intravenously every 8 to 24 hours (total 5 to 15 mg/kg).
    b) CHRONIC TOXICITY
    1) ADULT DOSE
    a) 300 to 400 mg/day orally (in single doses of 100 to 200 mg). The dose may be increased in severe toxicity (Arbeitsgruppe BGVV, 1996; Prod Info DIMAVAL(R) oral capsules, 2004).
    c) DMPS/ADVERSE REACTIONS
    1) Chills, fever, and allergic skin reactions such as itching, exanthema or maculopapular rash are possible (Hla et al, 1992; Prod Info DIMAVAL(R) oral capsules, 2004). Cardiovascular effects such as hypotension, nausea, dizziness or weakness may occur with too rapid injection of DMPS. Hypotensive effects are irreversible at very high doses (300 mg/kg) (Prod Info DIMAVAL(R) oral capsules, 2004; Prod Info Dimaval(R) intravenous intramuscular injection solution, 2013).
    3) SOURCES
    a) DMPS is not FDA-approved, but is available outside of the US from Heyl Chem-pharm Fabrik in Germany (Prod Info Dimaval(R) intravenous intramuscular injection solution, 2013; Prod Info DIMAVAL(R) oral capsules, 2004). In the US it may be obtained from some compounding pharmacies.
    4) EFFICACY
    a) It has been used to treat vapor exposures, intravenous exposures, inorganic salt ingestions, intraperitoneal exposures, and button battery ingestions (Torres-Alanis et al, 1997). It can be used orally, intravenously, or intramuscularly.
    5) Ashton et al (1992) reported a patient who injected approximately 270 grams of metal, was treated for 4 years, and survived. Blood mercury concentration was over 1600 mcg/L; urine levels over 73,500 mcg/L.
    6) Administration of 300 mg of DMPS orally increased mean urinary mercury excretion of volunteers with dental amalgams from 0.7 to 17.2 mcg (Aposhian et al, 1992). DMPS has been shown to increase urinary mercury excretion after exposure to mercurous chloride and elemental mercury (Gonzales-Ramirez et al, 1995; Maiorino et al, 1996; Gonzales-Ramirez et al, 1998; Torres-Alanis et al, 1995).
    7) ADVERSE REACTIONS
    a) SKIN REACTIONS - Urticaria, maculopapular rash, and erythema multiforme (p 13).
    H) ACETYLCYSTEINE
    1) N-acetylcysteine (15 mg/kg/day) and chelation therapy were used in 21 children with mercury exposure and high mercury blood or urine concentrations. After about 2 weeks of therapy, all blood and urine mercury concentrations of 20 patients were in the reference range. One patient required about one month of continued chelation therapy (Akyildiz et al, 2012).
    I) ACUTE LUNG INJURY
    1) ONSET: Onset of acute lung injury after toxic exposure may be delayed up to 24 to 72 hours after exposure in some cases.
    2) NON-PHARMACOLOGIC TREATMENT: The treatment of acute lung injury is primarily supportive (Cataletto, 2012). Maintain adequate ventilation and oxygenation with frequent monitoring of arterial blood gases and/or pulse oximetry. If a high FIO2 is required to maintain adequate oxygenation, mechanical ventilation and positive-end-expiratory pressure (PEEP) may be required; ventilation with small tidal volumes (6 mL/kg) is preferred if ARDS develops (Haas, 2011; Stolbach & Hoffman, 2011).
    a) To minimize barotrauma and other complications, use the lowest amount of PEEP possible while maintaining adequate oxygenation. Use of smaller tidal volumes (6 mL/kg) and lower plateau pressures (30 cm water or less) has been associated with decreased mortality and more rapid weaning from mechanical ventilation in patients with ARDS (Brower et al, 2000). More treatment information may be obtained from ARDS Clinical Network website, NIH NHLBI ARDS Clinical Network Mechanical Ventilation Protocol Summary, http://www.ardsnet.org/node/77791 (NHLBI ARDS Network, 2008)
    3) FLUIDS: Crystalloid solutions must be administered judiciously. Pulmonary artery monitoring may help. In general the pulmonary artery wedge pressure should be kept relatively low while still maintaining adequate cardiac output, blood pressure and urine output (Stolbach & Hoffman, 2011).
    4) ANTIBIOTICS: Indicated only when there is evidence of infection (Artigas et al, 1998).
    5) EXPERIMENTAL THERAPY: Partial liquid ventilation has shown promise in preliminary studies (Kollef & Schuster, 1995).
    6) CALFACTANT: In a multicenter, randomized, blinded trial, endotracheal instillation of 2 doses of 80 mL/m(2) calfactant (35 mg/mL of phospholipid suspension in saline) in infants, children, and adolescents with acute lung injury resulted in acute improvement in oxygenation and lower mortality; however, no significant decrease in the course of respiratory failure measured by duration of ventilator therapy, intensive care unit, or hospital stay was noted. Adverse effects (transient hypoxia and hypotension) were more frequent in calfactant patients, but these effects were mild and did not require withdrawal from the study (Wilson et al, 2005).
    7) However, in a multicenter, randomized, controlled, and masked trial, endotracheal instillation of up to 3 doses of calfactant (30 mg) in adults only with acute lung injury/ARDS due to direct lung injury was not associated with improved oxygenation and longer term benefits compared to the placebo group. It was also associated with significant increases in hypoxia and hypotension (Willson et al, 2015).
    J) Treatment should include recommendations listed in the ORAL EXPOSURE section when appropriate.

Eye Exposure

    6.8.1) DECONTAMINATION
    A) ELEMENTAL MERCURY
    1) Mercury droplets may be absorbed after conjunctival contact (Grant, 1986). Exposed eyes should be immediately irrigated with copious amounts of room temperature water for at least 15 minutes, occasionally lifting upper and lower eyelids.
    2) If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, an ophthalmologic examination should be considered.

Case Reports

    A) ADULT
    1) ROUTE OF EXPOSURE
    a) PERITONEAL EXPOSURE
    1) A 64-year-old female with peripheral vascular disease, Crohn's disease and intestinal obstruction was inadvertently exposed to elemental mercury after the tube reservoir of a Cantor tube ruptured (weighted with at least 10cc of mercury). Immediate surgical attempts to remove the liquid metal were not performed. Approximately 6 weeks after discharge, the patient developed formication and pruritus, and over the next 6 months she developed fatigue, insomnia, transient alopecia totalis, dizziness, continued abdominal pain, choking, and unilateral, burning headaches. These symptoms persisted along with increasing irritability (Haas et al, 2003).
    2) Approximately, two years after the initial exposure, an abdominal x-ray was performed because of recurrent Crohn's-related abdominal pain. Metallic densities were noted, and the mercury level was 485 mcg/L (normal less than 20) and the patient was informed of the mercury exposure. Two courses of chelation therapy (done at the patient's request) were performed without any significant change in mercury levels. Surgical intervention was considered, but the mercury was loculated in scar tissue and was not amenable to surgical removal. During the next 5 years, the patient's overall health declined (worsening peripheral vascular illness), but no cognitive impairments were noted and tremor was noted only a year before her death (due to inoperable lung cancer). The authors were uncertain why the patient did not display more severe effects due to mercury exposure, and tremor was notably absent until almost 8 years after exposure (Haas et al, 2003).
    b) SMELTING, AMALGAM HANDLING
    1) Four adult occupants of a private home developed shortness of breath 24 hours after exposure to mercury vapors during the smelting of silver from dental amalgam (Kanluen & Gottlieb, 1991).
    2) Respiratory failure and death resulted despite chelation with dimercaprol.
    3) Findings at postmortem included severe diffuse alveolar damage with varying amounts of fibrosis, acute proximal renal tubular necrosis, vacuolar hepatotoxicity, and CNS findings of multifocal ischemic necrosis, gliosis, and vasculitis.
    4) Crude gold refining operations often use the mercury amalgam method and may result in significant exposure. A number of studies have examined these exposures in detail (Drake et al, 2001; van Straaten, 2000).
    5) Chronic exposure over several months to mercury vapors from gold extraction methods resulted in progressive confusion in a 24-year-old. The blood and urine mercury levels were 12 mcg% and 720 mcg/24 hour, respectively (Shamley & Sack, 1989).
    c) AMALGAM EXPOSURE, DENTAL WORKERS
    1) Chronic exposure to mercury from the grinding of old amalgam restorations resulted in toxicity in a 60-year-old female. Urine levels of 50 to 80 mcg/L were extrapolated from levels obtained 3 months post dental treatment (Taskinen et al, 1989).
    2) Mercury exposure is dependent upon the design of dental equipment and particularly the design and discharge locations (inside versus outside) of dental aspirators. These devices appear to contribute significantly to unacceptable breathing zone mercury exposures in dental workers (Stonehouse & Newman, 2001). While amalgamators can also become contaminated with mercury, they do not appear to make a significant contribution to breathing zone exposures (Roberts et al, 2001).
    3) LACK OF EFFECT - A study of dental nurses exposed to silver amalgam 30 years previously found no differences in neurobehavioral test scores compared to controls. Overall self-reported health status was similar between groups (Jones et al, 2007).
    d) EXPOSURE FROM INJECTION, IMPLANTATION
    1) A 27-year-old male was admitted to an emergency department complaining of pain and swelling resulting from subcutaneous self-injection of mercury.
    a) The area was incised exposing a deposit of mercury. Radiographs revealed mercury remaining in the wound as well as mercury emboli in both lungs. Blood and urinary mercury levels were described as elevated but not toxic.
    b) One month later, he returned complaining of flu-like symptoms and headache, and specks of mercury were visible on skull radiographs. Treatment with penicillamine was initiated leading to full recovery (Roden & Fraser-Moodie, 1993).
    B) PEDIATRIC
    1) ROUTE OF EXPOSURE
    a) INGESTION
    1) A 3-year-old girl who had swallowed mercury from a broken thermometer experienced no apparent adverse effects (Martijn et al, 1990). Mercury droplets were identified by abdominal x-ray. Oral laxatives and a laxative diet were provided, with follow-up radiographic studies.
    b) SMELTER, ENVIRONMENTAL EXPOSURE
    1) A 20-month-old infant developed severe neurologic toxicity from 2 month exposure to elemental mercury (Swinehart, 1988). The child presented with fever, irritability, tremor, a chronically ill appearance, and refused to walk. Urine mercury levels were 0.6 mg/L.
    2) The family home was located about 500 feet from a mercury smelter; the father was a furnace operator at the smelter.
    c) SPILLS, OTHER ENVIRONMENTAL
    1) Heating or air oxidation may occur during repeated vacuuming of an elemental mercury spill, forming mercuric oxide (Zelman, 1989).
    2) Liquid mercury spilled in the home was associated with the development of symptoms in a 20-month-old female (Taylor et al, 1989).
    3) A mercury spill (0.5 to 1 oz) in the home resulted in severe symptoms (ataxia, fatigue, headache, irritability, hallucinations) in 2 of 3 siblings. All 3 children required treatments with BAL and NAP (Florentine & Sanfilippo, 1991).
    4) Chronic exposure over 5 months to mercury from repeated vacuuming of a mercury contaminated carpet resulted in weakness, lethargy, weight loss, insomnia, and diminished tendon reflexes in a 14-year-old boy. The serum and urine mercury levels were 186 and 3972 mmol/L, respectively (Zelman, 1989).
    5) A middle school was contaminated with liquid mercury when a student brought approximately 60 mL into the building. The mercury was handled by at least 62 students. Following discovery of the mercury, the school was evacuated and exposed students underwent surface decontamination, 12 hours after initial exposure. Peak airborne mercury concentrations exceeded 50 mcg/m(3) near the lockers where students stored the mercury. Students who were in contact with the mercury had spot urine levels that were higher than non-exposed students (0.50 mcg/L vs 0.33 mcg/L). No significant health effects were reported (Azziz-Baumgartner et al, 2007).
    6) Two patients developed acrodynia with neuropsychiatric impairment after a large spill of elemental mercury within their apartment (CDC, 1990a).
    7) A family of four developed toxic mercury blood levels after vacuuming 2.3 kg of liquid mercury spilled on a hall closet carpet (Schwartz et al, 1992).
    a) The 3.3-year-old child presented 2 weeks after the spill with dry cough, fever, headache, and a generalized maculopapular rash. The admission mercury blood level was found to be 151 mcg/L. The rash and fever improved over 2 days, and the child was discharged.
    b) Two weeks later the rash increased, and cough, chills, fever, bleeding from nose and gums, and cervical lymphadenopathy were present. Platelets were markedly decreased. He was diagnosed with acute ITP and treated with prednisone and DMSA. The child's 5- year-old brother was also symptomatic (fever, cough, rash).
    8) A 20-month-old, 11 kilogram female was found to have a whole blood mercury of 49 micrograms/Liter when admitted for a 6 week illness (anorexia, irritability, insomnia, stomatitis, and red, painful hands and feet).
    a) The source of exposure was traced to a small vial containing approximately 5 milliliters of elemental mercury that was spilled on the rug 2 weeks prior to her onset of symptoms.
    b) No other family members had symptoms and the mother's whole blood mercury concentration was 5 micrograms/Liter (Taylor et al, 1989).
    9) Three siblings developed acrodynia attributed to a thermometer broken in the children's bedroom 8 months earlier (Muhlendahl, 1990). Peak urinary mercury concentrations ranged from 137.4 to 266.3 mcg/L.
    10) A 3-year-old with clinical manifestation consistent with mercury poisoning was found to have a random urine sample containing 160 micrograms/liter of mercury without a known mercury exposure.
    a) The patient and his family had been living for 3 months in a house in which the previous resident had collected elemental mercury. A mercury vapor analyzer detected mercury concentrations of 20 to 60 micrograms/cubic meter in 5 rooms and 2 bathrooms (CDC, 1989).
    11) The 17-week pregnant mother of this child was asymptomatic, but had a 24-hour urine mercury level of 230 mcg/L. The urine mercury declined throughout gestation and was not detectable at 36 weeks. The neonate was normal at birth; the only abnormal value was a hair mercury level of 3 ng/g (normal less than 0.0008) (Thorp et al, 1992).
    12) Symptomatic mercury vapor intoxication has developed after chronic home exposure to mercury spills of as little as 5 milligrams of elemental mercury or the amount contained in a thermometer (Taylor et al, 1989; Muhlendahl, 1990; CDC, 1989).
    13) A 14-year-old boy was admitted for symptoms suggesting PHEOCHROMOCYTOMA, including irritability, insomnia, lethargy, profuse sweating, hypertension, tachycardia, and erythema with desquamation (Henningsson et al, 1993).
    a) His condition continued to deteriorate until it was discovered that he had been chronically exposed to elemental mercury from a contaminated heater coil. He was treated with BAL with symptomatic improvement.
    b) The boy's parents developed tremors, weakness, erythema, memory loss, sweating, and palpitations, which resolved with penicillamine therapy and decontamination of the home.
    14) Foulds (1987) reported a case of ACRODYNIA in a 30-month-old who had a 2 month history of progressive irritability and pruritus. Classic manifestations of irritability, lethargy, hypotonia, pruritus, erythema with desquamation, tachycardia, and hypertension were present (Foulds et al, 1987).
    15) HEPATIC structure and function were determined in 62 persons who were chronically exposed in their residence for an average of 16 years to an estimated annual metallic mercury intake exceeding 24 kg. Details of the study were limited in this abstract (Winnik, 1994).
    16) NEUROPSYCHOLOGICAL effects were reported in 2 adolescents exposed to mercury vapors (50 to 400 mcg/m3) for 3 months (Yeates & Mortensen, 1994). The source of the vapors was an improperly cleaned elemental mercury spill. The children received a two to three courses of 2,3-dimercaptosuccinic acid (DMSA) chelation therapy. Psychological evaluations were performed initially and after 1 year.
    a) The study was confounded by a history of poor academic achievement, low IQ, and/or reading and language difficulties prior to the mercury exposure.
    17) Intermittent dermatitis involving the eye lids, neck and hands occurred in a dental nurse who had positive patch test responses to metallic mercury and organic mercury compounds (Kanerva et al, 1993). The nurse had prior dermal exposure to uncured dental amalgams.

Summary

    A) TOXICITY: Exposure to broken fluorescent light bulbs containing mercury (4 to 6 mg) is not expected to produce toxicity. Thermometers contain about 500 mg of elemental mercury and can cause symptomatic poisoning if vaporized by vacuuming. Young children have developed toxicity after less than 2 weeks of exposure to mercury generated by a glass thermometer that broke and spilled on carpet, and after the spillage of 0.5 to 1 ounce of mercury in a home. The amount of ingested mercury that would be fatal to a man is estimated at 100 grams (1429 mg/kg). A man ingested 500 g (66 mL) of elemental mercury (quicksilver) in a suicide attempt, but survived following supportive care.

Minimum Lethal Exposure

    A) ADULT
    1) The amount of ingested mercury that would be fatal to a man is estimated at 100 grams (1429 mg/kg) ((HSDB, 2002)). A daily dose of 75 mg mercury in drinking water is also thought to be fatal ((OHM/TADS, 2002)).
    2) A 30-year-old woman presented with mercury toxicity after self-injection and ingestion of approximately 500 g of mercury from 37 broken fever thermometers. Despite supportive treatment, she developed lung embolization complicated by acute respiratory distress syndrome (ARDS), toxic dermatitis, anemia, and mild hepato-renal impairment, and died 30 days after presentation (DePalma et al, 2008).
    3) Patients having mercury concentrations in the blood and urine of 0.4 to 0.9 mg/L and 0.5 to 1.6 mg/L, respectively, died from acute mercury vapor poisoning (Baselt, 2000).
    4) Four adults (2 men and 2 women, ranging in age from 40 to 88 years old) died following exposure to mercury vapors while smelting silver from dental amalgam in their home (Kanluen & Gottlieb, 1991). Measurements of the ambient air in the home eleven to eighteen days after the initial exposure revealed mercury concentrations ranging from 786 to 912 mg/m(3) (ACGIH, 1996).
    5) Systemic mercury toxicity and death followed rupture of a mercury-containing Miller-Abbott intestinal decompression tube (Bredfeldt & Moeller, 1978; Kurt, 1984).
    B) PEDIATRIC
    1) A three year old girl died approximately 2 months after playing with elemental mercury. The mercury concentrations in her tissues at the time of death were: brain, 1.3 mg/kg; lung, 3.7 mg/kg; liver, 3.9 mg/kg; kidney, 14 to 30 mg/kg; antemortem urine, 0.16 to 0.86 mg/L (Baselt, 2000).

Maximum Tolerated Exposure

    A) ADULT
    1) CASE REPORT: A 55-year-old man presented to the ED after ingesting 500 g (66 mL) of elemental mercury (quicksilver). Before presentation, he also drank an unknown amount of alcohol and attempted suicide by inhaling propane from a gas bottle. Abdominal x-ray radiographs revealed a large amount of radio-opaque liquid in his stomach. He received a bowel evacuation regimen, containing polyethylene glycol and activated charcoal, and his serum mercury concentrations peaked at 511 nM (occupational exposure safety limit: less than 75 nM, based on inhalational exposure) about 24 hours postingestion. At this time, he also received a single daily oral dose of succimer (10 mg/kg). Because of difficulties with GI evacuation, fluoroscopy was used for bowel emptying and abdominal x-ray radiographs revealed new mercury globules, suggesting the reingestion of fecal mercury. Following further supportive care, including psychiatric treatment to discontinue the fecal mercury reingestion, his mercury levels gradually decreased and he was discharged on day 5 (Mitenko, 2014).
    2) CASE REPORT: A 43-year-old man presented to the ED with severe abdominal pain and persistent vomiting following the ingestion of 200 mL of elemental liquid mercury in a suicide attempt. His chest x-ray revealed small amounts of mercury in lower lung fields bilaterally, indicating aspiration. He was treated with IV fluids, opioid analgesics, and antiemetic medications before being transferred to a negative pressure side room to reduce the risk of mercury inhalation by hospital staff. A nasogastric tube was inserted and 115 mL of mercury was aspirated from his stomach leading to significant improvement in patient's symptoms and resolution of vomiting. The patient's blood mercury concentrations continued to rise by day 2 (675 nmol/L on admission and 934 nmol/L on day 2), suggesting continual systemic absorption from the lungs and his 24-hour urine mercury concentration was also elevated (14365 nmol/day). At this time, he was treated with IV 2,3-dimercaptopropane-1-sulfonate (DMPS, Dimaval; 30 mg/kg/day in 8 divided doses for 6 days), leading to improved blood and urinary mercury concentrations that continued to decrease 5 days later. The patient was subsequently discharged home after psychiatric review (Dawson et al, 2013).
    3) Fluorescent light bulbs contain a very small amount (4 to 6 mg) of mercury inside a glass tubing. In contrast, a glass thermometer contains about 500 mg of mercury (US Environmental Protection Agency, 2007; US Environmental Protection Agency, 2007). Health effects are not expected from acute exposure to a broken bulb.
    4) A man ingested as much as 204 grams of elemental mercury with little effect (Wright et al, 1980).
    5) After a 20 mL IV injection of mercury, a 14-year-old boy experienced emboli in both lung fields, metal densities in the abdomen, and small mercury pools in the right ventricle. He also endured an elevated temperature, difficulty breathing, general malaise, and pleuritic chest pain with shortness of breath ((HSDB, 2002)).
    6) After working for three years at a thermometer plant, nine workers experienced tremors, rigidity, loss of memory, blurred vision, and auditory and visual hallucinations. Permanent defects in recent memory, thought to be related to generalized cerebral cortical dysfunction, were severe in two workers and moderate in seven (ACGIH, 1991).
    7) Deliberate intravenous injection of 20 mL mercury by a 14-year-old boy resulted in mercury emboli in both lungs, severely reduced pulmonary function, elevated temperature and general malaise, but was not fatal ((HSDB, 2002)).
    8) The toxic threshold of mercury through parenteral exposure is estimated at 40 to 270 g ((HSDB, 2002)).
    9) Large quantities of mercury have been accidentally released into the gastrointestinal tract during surgical manipulations without serious effect. Nonpersistent fistulous tracts were the only reported reaction ((HSDB, 2002)).
    10) Toxicity may be evident in populations exposed to mercury vapor concentrations of greater than 1.0 mg/m(3) for extended periods of time (Bingham et al, 2001).
    11) Blood mercury levels of 0.02 mg/L are considered acceptable (Baselt, 2000).
    12) Chlor-alkali workers exposed to mercury vapor concentrations from 0.05 to 0.10 mg/m(3) exhibited no overt signs of mercury intoxication. No abnormalities in perceptual, motor, memory or learning abilities were seen in workers chronically exposed to average concentrations of 25 mcg/m(3) mercury vapor (ACGIH, 1996).
    13) AMALGAMATION: Occupational exposures have been recognized by color changes on gold jewelry (amalgamation).
    B) PEDIATRIC
    1) Fluorescent light bulbs contain a very small amount (4 to 6 mg) of mercury inside a glass tubing. In contrast, a glass thermometer contains about 500 mg of mercury (US Environmental Protection Agency, 2007; US Environmental Protection Agency, 2007). Health effects are not expected from acute exposure to a broken bulb.
    2) An 8-month-old girl was successfully treated for acute mercury vapor intoxication with oxygen, IV injections of nafcillin sodium (100 mg/kg/day) ((HSDB, 2002)).
    3) An elemental mercury spill (0.5 to 1 ounce) in the home resulted in a mercury blood level of less than 1 mcg/dL and a urine level of 120 mcg/24 hours in a 4-year-old. Symptoms associated with these levels were severe (fever, insomnia, headache, ataxia, hallucinations, irritability) requiring treatment with BAL and NAP (Florentine & Sanfilippo, 1991).
    4) An 11-month-old and a 6-year-old developed rash, neurologic toxicity and hypertension 2 weeks after a thermometer was broken in their bedroom resulting in mercury spilling on the carpet (Velzeboer et al, 1997).
    C) NON-HUMAN DATA
    1) The kidneys, liver, brain, heart, lung, and colon of rabbits have been severely damaged after exposure to 28.8 mg/m(3) mercury vapor for one four hour period ((HSDB, 2002)).
    2) Inhalation of mercury vapor by sheep and cattle is extremely toxic, causing dyspnea and coughing, nasal discharge, fever, loss of appetite and, at times, bleeding of oral mucosa, dermatosis and nephritis ((HSDB, 2002)).

Serum Plasma Blood Concentrations

    7.5.2) TOXIC CONCENTRATIONS
    A) TOXIC CONCENTRATION LEVELS
    1) The urine and blood mercury levels of 8 family members, who were exposed to mercury vapors as a result of home gold ore processing, were as follows (Solis et al, 2000):
    Patient Age Spot Urine Hg level (mcg/L) 24 hr Urine Hg level (mcg/L) Blood Hg level (mcg/L)
    45 days 45 35 117
    13 months 190 120 160
    38 years 682 163 322
    58 years- 112 275
    3 years 210 161 -
    7 years 110 177 -
    10 years 575 485 -
    14 years 27 107-

    2) Two days following exposure to an elemental mercury spill, the blood mercury levels of 8 adolescents ranged from less than 4 mcg/L to 13 mcg/L (Anon, 2005).
    3) ADULTS
    a) CASE REPORT: A 34-year-old man presented with fever, vomiting, and hemoptysis 2 days after the self-injection of 25 mL of elemental mercury in a suicide attempt. On presentation, his plasma mercury concentration was 2625 mcg/L (upper limit of normal: 15 mcg/L). A chest x-ray revealed several metallic densities throughout both lung fields, with numerous mercury deposits in the pulmonary venous circulation, and in the right auricular and ventricular cavities. An abdominal x-ray revealed mercury embolism of renal arteries. Following the excision of all affected subcutaneous tissues, he received dimercaptosuccinic acid (10 mg/kg 3 times daily for 15 days); however, his blood mercury concentration did not decrease significantly. His serum creatinine concentrations were between 70 to 80 mcmol/L during the first month and it increased to 164 mcmol/L 2 years post-exposure. Within the next 3 years, he developed recurrent subcutaneous abscess with droplets of mercury, sensory motor polyneuropathy, and a toxic megacolon complicated by peritonitis. He developed dialysis dependant renal failure 4 years after exposure (Truche et al, 2012).
    b) A 42-year-old woman presented with a 2-year history of painful violaceous nodules and plaques on her right forearm and left anterior tibia. The patient who was injecting mercury to these sites for several years to treat HIV infection, also experienced nausea, vomiting, chronic nonlocalizing abdominal pain, weakness, headaches, and visual disturbances. Laboratory results showed a serum mercury concentration of 300 mcg/L (reference range, less than 5 mcg/L). Despite treatment with penicillamine for 3 months, her serum mercury concentration did not decrease. Her symptoms improved after intraoperative C-arm fluoroscopy-assisted surgical debridement of the areas (Altmeyer et al, 2011).
    c) Two years after a woman injected herself with 5 mL of elemental mercury, her serum mercury level was 6 mcg/dL (normal, 0.06 to 5.9 mcg/dL) and urinary mercury level was markedly high at 80.0 mcg/L (normal, less than 20 mcg/L). She was treated with D-penicillamine for 12 days after the initial exposure, but she developed disabling generalized myoclonus of cortical origin and gait ataxia 2 years after the exposure. Her symptoms progressed over the next 2 years and improved after the mercury deposits were cleared surgically from the injection site (Ragothaman et al, 2007).
    d) A 33-year-old woman experienced nausea, vomiting, and abdominal pain after ingestion of approximately 1000 mL (1.3 kg) of elemental mercury. Initial blood and urine mercury concentrations were 180 mcg/L and 653 mcg/L, respectively. No neurological or renal toxicity was reported (Song & Li, 2007).
    e) A 49-year-old ingested 200 mL (2709 g) of elemental mercury and aspirated during gastric lavage. Multiple mercury droplets were detectable on chest x-ray but no significant respiratory symptoms were reported. Whole blood mercury level peaked at 457 mcg/L 8 days later (Lech & Goszcz, 2006).
    f) The blood and urine mercury levels of 8 men (age, 35 to 54 years), who were exposed to mercury vapors while cutting pipes in a sulfuric acid plant, were greater than 5 mcg/dL (range 5.1 to 16.8 mcg/dL) and greater than 25 mcg/dL (range 28 to 442 mcg/L) , respectively (Hashimoto et al, 2001).
    g) A 61-year-old diabetic man developed neurotoxicity after repeated self-injection of unknown quantity of elemental mercury. His whole blood mercury and 24-hour urine concentrations were 321 mcg/L and 230 mcg/L, respectively (Schaumburg et al, 2009).
    h) A 27-year-old woman with a very high blood and urine mercury levels delivered a healthy infant 10 years after she injected approximately 3 mL of liquid metallic mercury into her left antecubital vein in a suicide attempt. Mercury levels at the beginning of pregnancy were: serum 216 ng/mL; urine 413 ng/mL; whole blood 209 ng/mL. Despite these high levels, the mother did not experience any neurological sequelae or long-term toxic damage from mercury exposure. On several follow-up visits, the infant's developmental neurobehavioral milestones and growth were appropriate for her age (Pugach & Clarkson, 2009).
    i) A 30-year-old woman presented with mercury toxicity after self-injection and ingestion of approximately 500 g of mercury from 37 broken fever thermometers. Despite supportive treatment, she developed lung embolization complicated by acute respiratory distress syndrome (ARDS), toxic dermatitis, anemia, and mild hepato-renal impairment, and died 30 days after presentation (DePalma et al, 2008).
    1) Blood (HgB), plasma (HgP), urine (HgU), and bronchoalveolar fluid (HgBF) mercury concentrations were obtained on presentation until day 19. On day 14, a chelation challenge test with succimer 300 mg in 3 equal doses was performed every 8 hours and HgB, HgP, and HgU levels were monitored after each dose. The HgU concentrations ranged from 422.5 to 7964 mcg/L (mean +/- standard deviation: 2509.82 +/- 2002.14 mcg/L) and HgB ranged from 366 to 1202 mcg/L (863.71 +/- 218.03). After DMSA, HgU levels increased (4481.50 +/- 2443.78 vs 1664.82 +/- 999.27 mcg/L (before DMSA), p less than 0.05), HgP levels decreased (886.8 +/- 300.18 vs 1229.75 +/- 293.89 mcg/L (before DMSA), p less than 0.05), and the urinary mercury clearance increased (medians of 8.85 vs 2.48 (before DMSA) mL/min, p less than 0.05)). The HgBF clearance had a mean value of 0.12 +/- 0.06 mL/min (range 0.04 to 0.27) (DePalma et al, 2008).
    4) CHILDREN
    a) A 2.5-year-old boy developed lethargy and respiratory distress after exposure to mercury vapor. His blood mercury level was 512 mcg/L and random urine mercury level was 165 mcg/L. Following supportive care, including treatment with D-penicillamine, NAC, and multivitamins, he recovered gradually (Sevketoglu et al, 2011).
    b) A 10-year-old boy developed acrodynia, seizures, and visual impairment after exposure to elemental mercury for 20 days. Approximately 4 months after the first exposure to elemental mercury, he was diagnosed with mercury poisoning; his whole blood mercury level and the 24-hour urinary mercury level were 27.7 mcg/L (normal <2 mcg/L) and 34.4 mcg/L (normal = 10 mcg/L), respectively. He was treated with dimercaprol (2 courses) and D-penicillamine. Following 35 days of supportive therapy, he was discharged home and followed as an out-patient. He recovered completely after 9 months of treatment without further sequelae (Abbaslou & Zaman, 2006).
    c) A 24-hour urine mercury of an 11-year-old girl with mercury poisoning was 21 mcg/L (reference value =/< 5 mcg/L) before chelation therapy. The highest concentration of urine mercury during chelation therapy was 97 mcg/L. She experienced back pain, weight loss, fatigue, behavioral disturbances, acrodynia, tremor, cachexia, and hypertension. Following chelation therapy with DMPS for 9 weeks, she recovered gradually (van der Linde et al, 2009).
    d) A middle school was contaminated with liquid mercury when a student brought approximately 60 mL into the building. The mercury was handled by at least 62 students. Following discovery of the mercury, the school was evacuated and exposed students underwent surface decontamination, 12 hours after initial exposure. Peak airborne mercury concentrations exceeded 50 mcg/m(3) near the lockers where students stored the mercury. Students who were in contact with the mercury had spot urine levels that were higher than non-exposed students (0.50 mcg/L vs 0.33 mcg/L). No significant health effects were reported (Azziz-Baumgartner et al, 2007).

Workplace Standards

    A) ACGIH TLV Values for CAS7439-97-6 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
    a) Adopted Value
    1) Mercury, elemental and inorganic forms, as Hg
    a) TLV:
    1) TLV-TWA: 0.025 mg/m(3)
    2) TLV-STEL:
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: A4
    2) Codes: BEI, Skin
    3) Definitions:
    a) A4: Not Classifiable as a Human Carcinogen: Agents which cause concern that they could be carcinogenic for humans but which cannot be assessed conclusively because of a lack of data. In vitro or animal studies do not provide indications of carcinogenicity which are sufficient to classify the agent into one of the other categories.
    b) BEI: The BEI notation is listed when a BEI is also recommended for the substance listed. Biological monitoring should be instituted for such substances to evaluate the total exposure from all sources, including dermal, ingestion, or non-occupational.
    c) Skin: This refers to the potential significant contribution to the overall exposure by the cutaneous route, including mucous membranes and the eyes, either by contact with vapors or, of likely greater significance, by direct skin contact with the substance. It should be noted that although some materials are capable of causing irritation, dermatitis, and sensitization in workers, these properties are not considered relevant when assigning a skin notation. Rather, data from acute dermal studies and repeated dose dermal studies in animals or humans, along with the ability of the chemical to be absorbed, are integrated in the decision-making toward assignment of the skin designation. Use of the skin designation provides an alert that air sampling would not be sufficient by itself in quantifying exposure from the substance and that measures to prevent significant cutaneous absorption may be warranted. Please see "Definitions and Notations" (in TLV booklet) for full definition.
    c) TLV Basis - Critical Effect(s): CNS impair; kidney dam
    d) Molecular Weight: Varies
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:
    b) Adopted Value
    1) Mercury, as Hg
    a) TLV:
    1) TLV-TWA: 0.025 mg/m(3)
    2) TLV-STEL:
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: A4
    2) Codes: Not Listed
    3) Definitions:
    a) A4: Not Classifiable as a Human Carcinogen: Agents which cause concern that they could be carcinogenic for humans but which cannot be assessed conclusively because of a lack of data. In vitro or animal studies do not provide indications of carcinogenicity which are sufficient to classify the agent into one of the other categories.
    c) TLV Basis - Critical Effect(s): CNS impair; kidney dam
    d) Molecular Weight: 200.59
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:
    c) Adopted Value
    1) Mercury, alkyl compounds, as Hg
    a) TLV:
    1) TLV-TWA: 0.01 mg/m(3)
    2) TLV-STEL: 0.03 mg/m(3)
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: Not Listed
    2) Codes: Skin
    3) Definitions:
    a) Skin: This refers to the potential significant contribution to the overall exposure by the cutaneous route, including mucous membranes and the eyes, either by contact with vapors or, of likely greater significance, by direct skin contact with the substance. It should be noted that although some materials are capable of causing irritation, dermatitis, and sensitization in workers, these properties are not considered relevant when assigning a skin notation. Rather, data from acute dermal studies and repeated dose dermal studies in animals or humans, along with the ability of the chemical to be absorbed, are integrated in the decision-making toward assignment of the skin designation. Use of the skin designation provides an alert that air sampling would not be sufficient by itself in quantifying exposure from the substance and that measures to prevent significant cutaneous absorption may be warranted. Please see "Definitions and Notations" (in TLV booklet) for full definition.
    c) TLV Basis - Critical Effect(s): CNS and PNS impair; kidney dam
    d) Molecular Weight: Varies
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:
    d) Under Study
    1) Mercury, alkyl compounds
    a) TLV:
    1) TLV-TWA:
    2) TLV-STEL:
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: Not Listed
    2) Codes: Not Listed
    3) Definitions: Not Listed
    c) TLV Basis - Critical Effect(s):
    d) Molecular Weight:
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:
    e) Adopted Value
    1) Mercury, aryl compounds, as Hg
    a) TLV:
    1) TLV-TWA: 0.1 mg/m(3)
    2) TLV-STEL:
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: Not Listed
    2) Codes: Skin
    3) Definitions:
    a) Skin: This refers to the potential significant contribution to the overall exposure by the cutaneous route, including mucous membranes and the eyes, either by contact with vapors or, of likely greater significance, by direct skin contact with the substance. It should be noted that although some materials are capable of causing irritation, dermatitis, and sensitization in workers, these properties are not considered relevant when assigning a skin notation. Rather, data from acute dermal studies and repeated dose dermal studies in animals or humans, along with the ability of the chemical to be absorbed, are integrated in the decision-making toward assignment of the skin designation. Use of the skin designation provides an alert that air sampling would not be sufficient by itself in quantifying exposure from the substance and that measures to prevent significant cutaneous absorption may be warranted. Please see "Definitions and Notations" (in TLV booklet) for full definition.
    c) TLV Basis - Critical Effect(s): CNS impair; kidney dam
    d) Molecular Weight: Varies
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:

    B) NIOSH REL and IDLH Values for CAS7439-97-6 (National Institute for Occupational Safety and Health, 2007):
    1) Listed as: Mercury compounds [except (organo) alkyls, as Hg]
    2) REL:
    a) TWA: Hg Vapor: 0.05 mg/m(3)
    b) STEL:
    c) Ceiling:
    d) Carcinogen Listing: (Not Listed) Not Listed
    e) Skin Designation: [skin]
    1) Indicates the potential for dermal absorption; skin exposure should be prevented as necessary through the use of good work practices and gloves, coveralls, goggles, and other appropriate equipment.
    f) Note(s): ,
    3) Listed as: Mercury (organo) alkyl compounds (as Hg)
    4) REL:
    a) TWA: 0.01 mg/m(3)
    b) STEL: 0.03 mg/m(3)
    c) Ceiling:
    d) Carcinogen Listing: (Not Listed) Not Listed
    e) Skin Designation: [skin]
    1) Indicates the potential for dermal absorption; skin exposure should be prevented as necessary through the use of good work practices and gloves, coveralls, goggles, and other appropriate equipment.
    f) Note(s):
    5) IDLH:
    a) IDLH: 10 mg Hg/m3 (as Hg)
    b) Note(s): Not Listed
    6) IDLH:
    a) IDLH: 2 mg Hg/m3 (as Hg)
    b) Note(s): Not Listed

    C) Carcinogenicity Ratings for CAS7439-97-6 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: Mercury, elemental and inorganic forms, as Hg
    a) A4 :Not Classifiable as a Human Carcinogen: Agents which cause concern that they could be carcinogenic for humans but which cannot be assessed conclusively because of a lack of data. In vitro or animal studies do not provide indications of carcinogenicity which are sufficient to classify the agent into one of the other categories.
    2) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: Mercury, as Hg
    a) A4 :Not Classifiable as a Human Carcinogen: Agents which cause concern that they could be carcinogenic for humans but which cannot be assessed conclusively because of a lack of data. In vitro or animal studies do not provide indications of carcinogenicity which are sufficient to classify the agent into one of the other categories.
    3) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Mercury, alkyl compounds, as Hg
    4) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Mercury, alkyl compounds
    5) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Mercury, aryl compounds, as Hg
    6) EPA (U.S. Environmental Protection Agency, 2011): D ; Listed as: Mercury, elemental
    a) D : Not classifiable as to human carcinogenicity.
    7) IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): 3 ; Listed as: Mercury and inorganic mercury compounds
    a) 3 : The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.
    8) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Mercury compounds [except (organo) alkyls, as Hg]
    9) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Mercury (organo) alkyl compounds (as Hg)
    10) MAK (DFG, 2002): Category 3B ; Listed as: Mercury (metallic mercury and inorganic mercury compounds)
    a) Category 3B : Substances for which in vitro or animal studies have yielded evidence of carcinogenic effects that is not sufficient for classification of the substance in one of the other categories. Further studies are required before a final decision can be made. A MAK value can be established provided no genotoxic effects have been detected. (Footnote: In the past, when a substance was classified as Category 3 it was given a MAK value provided that it had no detectable genotoxic effects. When all such substances have been examined for whether or not they may be classified in Category 4, this sentence may be omitted.)
    11) MAK (DFG, 2002): Category 3B ; Listed as: Mercury, organic compounds
    a) Category 3B : Substances for which in vitro or animal studies have yielded evidence of carcinogenic effects that is not sufficient for classification of the substance in one of the other categories. Further studies are required before a final decision can be made. A MAK value can be established provided no genotoxic effects have been detected. (Footnote: In the past, when a substance was classified as Category 3 it was given a MAK value provided that it had no detectable genotoxic effects. When all such substances have been examined for whether or not they may be classified in Category 4, this sentence may be omitted.)
    12) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    D) OSHA PEL Values for CAS7439-97-6 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Listed as: Mercury (aryl and inorganic) (as Hg)
    2) Table Z-1 for Mercury (aryl and inorganic) (as Hg):
    a) 8-hour TWA:
    1) ppm:
    a) Parts of vapor or gas per million parts of contaminated air by volume at 25 degrees C and 760 torr.
    2) mg/m3:
    a) Milligrams of substances per cubic meter of air. When entry is in this column only, the value is exact; when listed with a ppm entry, it is approximate.
    3) Ceiling Value:
    4) Skin Designation: No
    5) Notation(s): Not Listed
    3) Listed as: Mercury (organo) alkyl compounds (as Hg)
    4) Table Z-1 for Mercury (organo) alkyl compounds (as Hg):
    a) 8-hour TWA:
    1) ppm:
    a) Parts of vapor or gas per million parts of contaminated air by volume at 25 degrees C and 760 torr.
    2) mg/m3:
    a) Milligrams of substances per cubic meter of air. When entry is in this column only, the value is exact; when listed with a ppm entry, it is approximate.
    3) Ceiling Value:
    4) Skin Designation: No
    5) Notation(s): Not Listed
    5) Listed as: Mercury (vapor) (as Hg)
    6) Table Z-1 for Mercury (vapor) (as Hg):
    a) 8-hour TWA:
    1) ppm:
    a) Parts of vapor or gas per million parts of contaminated air by volume at 25 degrees C and 760 torr.
    2) mg/m3:
    a) Milligrams of substances per cubic meter of air. When entry is in this column only, the value is exact; when listed with a ppm entry, it is approximate.
    3) Ceiling Value:
    4) Skin Designation: No
    5) Notation(s): Not Listed
    7) Table Z-2 for Mercury (Z37.8-1971):
    a) 8-hour TWA:
    b) Acceptable Ceiling Concentration: 1 mg/10m(3)
    c) Acceptable Maximum Peak above the Ceiling Concentration for an 8-hour Shift:
    1) Concentration:
    2) Maximum Duration:
    d) Notation(s): Not Listed

Toxicity Information

    7.7.1) TOXICITY VALUES
    A) References: ITI, 1995 Lewis, 2000 RTECS, 2002
    1) TCLo- (INHALATION)HUMAN:
    a) 44,300 mcg/m(3) for 8H -- muscle weakness, liver changes, increase in body temperature
    b) 150 mcg/m(3) for 46D -- wakefulness, anorexia, gastrointestinal hypermobility, diarrhea
    2) TCLo- (INHALATION)MOUSE:
    a) male, 146 mcg/m(3) for 2H at 9W prior to mating -- spermatogenesis, other paternal effects
    3) TCLo- (INHALATION)RAT:
    a) female, 300 mcg/m(3) for 4H at 7-21D of pregnancy -- central nervous system effects
    b) male, 890 ng/m(3) for 24H, 16W prior to mating -- spermatogenesis, including genetic material, sperm morphology, motility and count
    c) 8 mcg/m(3) for 6.5H for 41W, Intermittent -- alteration of behavorial conditioning
    d) 4 mg/m(3) for 2H for 11D, Intermittent -- degenerative changes to the brain and coverings, changes to the kidney, bladder and ureter, biochemical enzyme changes
    e) 17 mg/m(3) for 3H for 30D, Continuous -- degenerative changes to the brain and coverings, alterations of behavorial and operant conditioning
    f) 1 mg/m(3) for 24H for 5W, Continuous -- proteinuria
    g) female, 1 mg/m(3) for 24H, at 1-20D of pregnancy -- fetotoxicity
    h) male, 7440 ng/m(3) for 24H, 16W prior to mating -- post-implantation mortality

Toxicologic Mechanism

    A) Mercury ions bind to sulfhydryl groups and subsequently may alter the structure and function of key proteins and enzymes. Cellular metabolism may be impaired by mercury binding to amines and phosphoryl groups (US DHHS, 1992).
    B) Kidney damage following mercury vapor exposure is believed to be mediated by an autoimmune mechanism by which inorganic mercury stimulated T lymphocytes produce antibodies that damage the glomeruli (Clarkson, 1990).

Physical Characteristics

    A) Mercury is an extremely heavy, odorless, silver-colored liquid (Bingham et al, 2001; ITI, 1995; Lewis, 2000; NIOSH , 2002).
    B) In its solid form, mercury is a ductile, malleable tin-white mass that can be cut with a knife (Lewis, 2000).
    C) Mercury is a liquid at 15 degrees C and 1 atm (CHRIS , 2002).

Molecular Weight

    A) 200.59

Other

    A) ODOR THRESHOLD
    1) odorless ((HSDB, 2002))

Clinical Effects

    11.1.1) AVIAN/BIRD
    A) Only about 0.01% of elemental mercury is absorbed via the GI tract so elemental mercury is fairly low in toxicity when ingested. If it becomes imbedded in tissues (as may occur if a rectal thermometer breaks while inserted) it may cause toxicity (Beasley et al, 1990).
    1) Organomercurials and inorganic mercury salts are more commonly associated with ACUTE toxicity (mercury toxicosis) in animals than exposure to elemental mercury (Osweiler & Hook, 1986).
    2) Muscle incoordination, ataxia, hyperesthesia, tremor, seizures, coma, skin and hair changes, and gastrointestinal disburbances (diarrhea, vomiting, anorexia) with subsequent fluid and electrolyte losses have been reported (Beasley et al, 1990).
    3) SUBACUTE OR CHRONIC TOXICITY is more common, after exposure periods of several days or longer. Neurologic, GI, renal, and dermal effects are seen (Beasley et al, 1990).
    11.1.2) BOVINE/CATTLE
    A) Organomercurials and inorganic mercury salts are more commonly associated with acute toxicity (mercury toxicosis) in animals than elemental mercury exposure. Ingestion of batteries which contain elemental mercury has been associated with mercury toxicosis in some animals (Osweiler & Hook, 1986).
    1) Clinical signs of mercury toxicosis (associated chiefly with organomercurials and inorganic mercury salts) may include stomatitis, salivation, hemorrhagic or necrotic enteritis, decreased appetite, weakness, and hematuria. Skin and hair changes may be noted. Severe neurological effects may also occur in cattle following organomercury exposure (Osweiler & Hook, 1986).
    11.1.9) OVINE/SHEEP
    A) Organomercurials and inorganic mercury salts are more commonly associated with acute toxicity in animals than exposure to elemental mercury. Ingestion of batteries which contain elemental mercury has been associated with mercury toxicosis in some animals (Osweiler & Hook, 1986).
    11.1.10) PORCINE/SWINE
    A) Organomercurials and inorganic mercury salts are more commonly associated with acute toxicity in animals than exposure to elemental mercury. Ingestion of batteries which contain elemental mercury has been associated with mercury toxicosis in some animals (Osweiler & Hook, 1986).
    1) Clinical signs of acute or subacute mercury toxicosis due principally to organomercurials and inorganic mercury salts include stomatitis, salivation, vomiting (in swine), hemorrhagic or necrotic enteritis, decreased appetite, weakness, and hematuria. White pigs may display erythema. Other skin and hair changes may be noted. Severe neurological effects have also been associated with organic mercury exposure in swine (Osweiler & Hook, 1986).

Treatment

    11.2.1) SUMMARY
    A) GENERAL TREATMENT
    1) Specific decontamination is not generally required following ingestion of elemental mercury unless the mercury remains in the gastrointestinal tract for a prolonged period of time. The following recommendations are principally intended for inorganic or organic mercury exposure.
    2) Begin treatment immediately.
    3) Keep animal warm.
    4) Sample vomitus, blood, urine, and feces for analysis.
    5) If skin exposure has occurred, wash animal thoroughly with a mild detergent and flush with copious amounts of water.
    6) ANIMAL POISON CONTROL CENTERS
    a) ASPCA Animal Poison Control Center, An Allied Agency of the University of Illinois, 1717 S. Philo Rd, Suite 36, Urbana, IL 61802, website www.aspca.org/apcc
    b) It is an emergency telephone service which provides toxicology information to veterinarians, animal owners, universities, extension personnel and poison center staff for a fee. A veterinary toxicologist is available for consultation.
    c) The following 24-hour phone number is available: (888) 426-4435. A fee may apply. Please inquire with the poison center. The agency will make follow-up calls as needed in critical cases at no extra charge.
    11.2.2) LIFE SUPPORT
    A) GENERAL
    1) MAINTAIN VITAL FUNCTIONS: Secure airway, supply oxygen, and begin supportive fluid therapy if necessary.
    11.2.4) DECONTAMINATION
    A) GASTRIC DECONTAMINATION
    1) SMALL ANIMALS
    a) Induce emesis with syrup of ipecac, 10 to 30 mL orally or hydrogen peroxide 5 to 25 mL orally repeated in 5 to 10 minutes if there is no response. DOGS ONLY may receive apomorphine 0.05 to 0.10 mg/kg IV, IM, or subcutaneously.
    b) Gastric lavage may be performed using tap water or normal saline.
    c) Administer activated charcoal, 5 to 50 g, orally, as a slurry in water.
    d) Then administer Milk of Magnesia 1 to 15 mL orally, mineral oil 2 to 15 mL orally, sodium sulfate 20%, 2 to 25 g orally or magnesium sulfate 20% 2 to 25 g orally, for catharsis.
    2) LARGE ANIMALS
    a) Give 250 to 500 g of activated charcoal in a water slurry, orally. Administer an oral cathartic: mineral oil (1 to 3 liters), 20% sodium sulfate (25 to 10,000 g), 20% magnesium sulfate (25 to 1,000 g), or Milk of Magnesia (20 to 30 mL).
    b) Ruminants (cattle and sheep) cannot be made to vomit. Horses should not be made to vomit.
    11.2.5) TREATMENT
    A) GENERAL
    1) Specific decontamination is not generally required following ingestion of elemental mercury unless the mercury remains in the gastrointestinal tract for a prolonged period of time. The following recommendations are principally intended for inorganic or organic mercury exposure.
    B) SMALL ANIMALS
    1) Emesis or gastric lavage followed by activated charcoal, 20% sodium thiosulfate (0.5 to 3 g), egg white, or tannic acid (200 to 500 mg in 30 to 60 mL water).
    2) Dimercaprol (BAL) 3 mg/kg IM every 4 hours days 1 and 2, four times daily on day 3, followed by twice daily on days 4 through 10. d-Penicillamine 11 mg/kg four times daily for 7 to 10 days, orally.
    C) LARGE ANIMALS
    1) Adsorbant. Dimercaprol (BAL): 3 mg/kg IM. Repeat every 4 hours for 2 days, then four times daily on 3rd day, then twice daily for 10 days until recovery. Supportive fluid and electrolyte therapy.

Range Of Toxicity

    11.3.2) MINIMAL TOXIC DOSE
    A) SPECIFIC TOXIN
    1) METALLIC MERCURY - Only 0.01% is absorbed via the GI tract so elemental mercury is fairly low in toxicity when ingested. If it becomes imbedded in tissues (as may occur if a rectal thermometer breaks while inserted) it may cause toxicity (Beasley et al, 1990).
    2) INORGANIC MERCURY - Causes toxicity in the horse at a dose of 8 to 10 grams. Chronic toxicity may result from ingestion of 0.4 milligram/kilogram/day over several weeks in horses (Beasley et al, 1990).
    3) ALKYL MERCURIC COMPOUNDS (SATURATED HYDROCARBONS) - Methyl and ethyl mercury are the most toxic forms of mercury. All forms of mercury sequestered in living organisms are converted by anaerobic bacteria into methyl mercury. This is also the form of mercury found in eggs as residue, regardless of the form of mercury ingested by the bird (Beasley et al, 1990).

Continuing Care

    11.4.1) SUMMARY
    11.4.1.2) DECONTAMINATION/TREATMENT
    A) GENERAL TREATMENT
    1) Specific decontamination is not generally required following ingestion of elemental mercury unless the mercury remains in the gastrointestinal tract for a prolonged period of time. The following recommendations are principally intended for inorganic or organic mercury exposure.
    2) Begin treatment immediately.
    3) Keep animal warm.
    4) Sample vomitus, blood, urine, and feces for analysis.
    5) If skin exposure has occurred, wash animal thoroughly with a mild detergent and flush with copious amounts of water.
    6) ANIMAL POISON CONTROL CENTERS
    a) ASPCA Animal Poison Control Center, An Allied Agency of the University of Illinois, 1717 S. Philo Rd, Suite 36, Urbana, IL 61802, website www.aspca.org/apcc
    b) It is an emergency telephone service which provides toxicology information to veterinarians, animal owners, universities, extension personnel and poison center staff for a fee. A veterinary toxicologist is available for consultation.
    c) The following 24-hour phone number is available: (888) 426-4435. A fee may apply. Please inquire with the poison center. The agency will make follow-up calls as needed in critical cases at no extra charge.
    11.4.2) DECONTAMINATION
    11.4.2.2) GASTRIC DECONTAMINATION
    A) GASTRIC DECONTAMINATION
    1) SMALL ANIMALS
    a) Induce emesis with syrup of ipecac, 10 to 30 mL orally or hydrogen peroxide 5 to 25 mL orally repeated in 5 to 10 minutes if there is no response. DOGS ONLY may receive apomorphine 0.05 to 0.10 mg/kg IV, IM, or subcutaneously.
    b) Gastric lavage may be performed using tap water or normal saline.
    c) Administer activated charcoal, 5 to 50 g, orally, as a slurry in water.
    d) Then administer Milk of Magnesia 1 to 15 mL orally, mineral oil 2 to 15 mL orally, sodium sulfate 20%, 2 to 25 g orally or magnesium sulfate 20% 2 to 25 g orally, for catharsis.
    2) LARGE ANIMALS
    a) Give 250 to 500 g of activated charcoal in a water slurry, orally. Administer an oral cathartic: mineral oil (1 to 3 liters), 20% sodium sulfate (25 to 10,000 g), 20% magnesium sulfate (25 to 1,000 g), or Milk of Magnesia (20 to 30 mL).
    b) Ruminants (cattle and sheep) cannot be made to vomit. Horses should not be made to vomit.

Kinetics

    11.5.1) ABSORPTION
    A) SPECIFIC TOXIN
    1) Inorganic mercury is well-absorbed from the lungs, but only 7% to 15% is absorbed through the skin and GI tract. Mercury salts can also bind to gut mucosa (Beasley et al, 1990).
    2) Elemental mercury can be absorbed via gut mucosa.
    3) Organic mercurials are absorbed via all routes, including dermal (Beasley et al, 1990).

Sources

    A) SPECIFIC TOXIN
    1) Elemental mercury is most commonly found in thermometers and barometers.
    2) Inorganic and organic mercurials are frequently found in manufactured products such as anti-fouling paints used on boat bottoms, batteries, and fungicides. Sewage sludge may contain mercury. The primary environmental form of mercury is methyl mercury, produced by anaerobic bacteria inside and outside of living organisms (Beasley et al, 1990).

General Bibliography

    1) 40 CFR 372.28: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Lower thresholds for chemicals of special concern. National Archives and Records Administration (NARA) and the Government Printing Office (GPO). Washington, DC. Final rules current as of Apr 3, 2006.
    2) 40 CFR 372.65: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Chemicals and Chemical Categories to which this part applies. National Archives and Records Association (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Apr 3, 2006.
    3) 49 CFR 172.101 - App. B: Department of Transportation - Table of Hazardous Materials, Appendix B: List of Marine Pollutants. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 29, 2005.
    4) 49 CFR 172.101: Department of Transportation - Table of Hazardous Materials. National Archives and Records Administration (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Aug 11, 2005.
    5) 62 FR 58840: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 1997.
    6) 65 FR 14186: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.
    7) 65 FR 39264: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.
    8) 65 FR 77866: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.
    9) 66 FR 21940: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2001.
    10) 67 FR 7164: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2002.
    11) 68 FR 42710: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2003.
    12) 69 FR 54144: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2004.
    13) AAR: Emergency Handling of Hazardous Materials in Surface Transportation, Bureau of Explosives, Association of American Railroads, Washington, DC, 2000.
    14) ACGIH: 1996 Supplements of the Sixth Edition of the ACGIH Documentation of the Threshold Limit Values and Biological Exposure Indices, Am Conference of Govt Ind Hyg, Inc, Cincinnati, OH, 1996.
    15) ACGIH: Documentation of the Threshold Limit Values and Biological Exposure Indices (Supplement), 6th ed, Am Conference of Govt Ind Hyg, Inc, Cincinnati, OH, 1996a.
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    17) AIHA: 2006 Emergency Response Planning Guidelines and Workplace Environmental Exposure Level Guides Handbook, American Industrial Hygiene Association, Fairfax, VA, 2006.
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