MOBILE VIEW  | 

COPPER

Classification   |    Detailed evidence-based information

Therapeutic Toxic Class

    A) Copper is an essential trace element. It occupies a position between nickel and zinc in group IB of the periodic table and is a noble metal, like gold and silver. Copper is the third most abundant trace element in the body and is an important catalyst for heme synthesis and iron absorption. Two patterns of human toxicity are reported: acute exposure to large doses or chronic poisoning from continued ingestion of smaller doses. Chronic copper toxicity, which is rare, affects mainly the liver.
    B) Metallic copper itself probably has little or no toxicity, although reports in the literature are conflicting. Copper salts produce toxicity. Soluble salts, such as copper sulfate, are strong irritants to skin and mucous membranes.

Specific Substances

    A) COPPER, METALLIC
    1) Allbri Natural Copper
    2) ANAC 110
    3) Arwood Copper
    4) Bronze Powder
    5) CDA 101
    6) CDA 102
    7) CDA 110
    8) CDA 122
    9) CE 1110
    10) Copper-Airborne
    11) Copper Bronze
    12) Copper Fume
    13) Copper M 1
    14) Copper Compounds
    15) Copper and Compounds
    16) Copper Metal Dusts
    17) Copper Metal Fumes
    18) Copper, Metallic Powder
    19) Copper-Milled
    20) Copper Powder
    21) Copper Slag-Airborne
    22) Copper Slag-Milled
    23) CU M3
    24) Cuprum (Latin)
    25) E 115 (Metal)
    26) 1721 Gold
    27) Gold Bronze
    28) Kafar Copper
    29) M 1
    30) M 3
    31) M 4
    32) M1 (Copper)
    33) M2 (Copper)
    34) M3 (Copper)
    35) M4 (Copper)
    36) M3R
    37) M3S
    38) OFHC Cu
    39) Raney Copper
    40) CAS 7440-50-8
    41) References: RTECS, 2001; HSDB, 2001; NIOSH, 2001
    RELATED COMPOUNDS (Copper I and Copper II compounds)
    1) Copper acetate
    2) Cupric acetate or cupric acetate, basic
    3) Cuprous acetate (acetic acid copper (1+) salt)
    4) Copper bromide
    5) Cupric bromide (CuBr2)
    6) Cuprous bromide (CuBr)
    7) Copper carbonate
    8) Cupric carbonate, basic (copper carbonate hydroxide)
    9) Copper chloride
    10) Cupric chloride (CuCl2)
    11) Cuprous chloride (CuCl)
    12) Copper cyanide
    13) Cuprous cyanide (CCuN)
    14) Copper fluoride
    15) Cupric fluoride (CuF2)
    16) Copper glycinate
    17) Copper iodide
    18) Cuprous iodide (CuI)
    19) Copper nitrate
    20) Cupric nitrate (CuN2O6)
    21) Copper oxide
    22) Copper oxychloride
    23) Cupric oxide (Black copper oxide) (CuO)
    24) Cuprous oxide (Red copper oxide) (Cu2O)
    25) Copper sulfate
    26) Cupric sulfate, basic (copper hydroxide sulfate)
    27) Cupric sulfide (CuS)

    1.2.1) MOLECULAR FORMULA
    1) Cu

Available Forms Sources

    A) FORMS
    1) INDUSTRIAL
    a) Industrially, copper is available as ingots, sheets, rods, wire, tubing, shot or powder, or in high purity (less than 10 ppm impurities) as single crystals or whiskers (HSDB , 2002; Lewis, 1997).
    b) Commercial copper is available in the following purities (HSDB , 2002):
    Electrolytic tough-pitch99.90% Cu
    Deoxidized99.90% Cu
    Oxygen-free99.92% Cu
    Silver-bearing99.90% Cu
    Arsenical99.68% Cu
    Free-cutting99.40 to 99.50% Cu

    B) SOURCES
    1) ISOTOPES: Copper occurs naturally in its elemental state. There are two naturally occurring stable isotopes, atomic weights 63 (69.09 percent) and 65 (30.91 percent), and nine artificial isotopes (atomic weights 58-62, 64, 66-68). It has valences 1 and 2. It is present in the earth's crust at 70 ppm and in seawater at 0.001 to 0.02 ppm (Budavari, 2000). It is the 26th-most-abundant element in the earth's crust (Harbison, 1998).
    2) ORE: Copper is also found in various ores including chalcopyrite, chalcocite, bornite, tetrahedrite, enargite, antlerite, azurite, azurmalachite, covellite, cuprite and malachite (Lewis, 1993; Budavari, 2000). The main ore is chalcopyrite (approximately 85 percent). Most copper mined today (about 85 percent) comes from ores containing 2 percent or less copper (Bingham et al, 2001). Copper is a noble metal, like silver and gold (Barceloux, 1999).
    3) BIOLOGICAL: Copper is an essential trace element in the human and animal diets, with many metabolic functions not fully understood, and is involved in plant metabolism. It occurs in biological complexes such as pheophytin (an analog of chlorophyll), hemocyanin, tyrosinase and ceruloplasmin (Baselt, 2000; Budavari, 2000). Copper is the third-most-abundant trace element in the human body (Barceloux, 1999).
    a) In humans, copper is found in many proteins (Bingham et al, 2001). It is essential for the function of many enzymes such as catalase and peroxidase, and is an important catalyst for heme synthesis and iron absorption (Barceloux, 1999; Goldfrank, 1998).
    b) Copper influences gene expression and is a cofactor for oxidative enzymes such as superoxide dismutase, cytochrome C oxidase and lysyl oxidase, as well as for aminolevulonic acid (Baxter et al, 2000a).
    C) USES
    1) Copper has excellent electrical conductivity, corrosion resistance, malleability and ductility, which make it very useful as an industrial metal (Baxter et al, 2000).
    2) As much as 75 percent of the copper used in the USA is for electrical conductors such as wire and switches (Bingham et al, 2001a; ILO, 1998). Copper is widely used in applications for which high electrical and thermal conductivity are needed. Copper whiskers are used in thermal and electrical composites (ACGIH, 1996a; Lewis, 1997a).
    3) Copper is used in important alloys such as bronze (copper alloyed with as much as 10 percent tin) and brasses (copper alloyed mainly with zinc). Monel metal, another copper alloys, is copper alloyed with nickel (Baxter et al, 2000; Lewis, 1997a).
    a) Copper alloyed with cadmium is used in electrical conductors; with magnesium and aluminum, in resistance wire and heating wire; with nickel, for chemical equipment; and with beryllium, in electrical contacts, springs, dies, bellows and welding links (Ashford, 1994).
    b) Brasses containing less than 58 percent copper have little application (Bingham et al, 2001a).
    4) Copper is useful in electroplated coatings and undercoatings for products made from nickel, chromium, and zinc, and in cooking utensils. Copper is also made into corrosion-resistant plumbing pipes, used in heating and roofing materials for building construction, and has applications in industrial machinery and in automobiles (HSDB, 2002; ILO, 1998; Lewis, 1997a).
    5) In agricultural applications, copper compounds (particularly copper sulfate) are used in insecticides, fungicides, herbicides, and algicides (Bingham et al, 2001a).
    6) Copper's contraceptive effects (as a spermatocide) are exploited for intrauterine devices. Its contraceptive effects permit the use of a smaller device, resulting in fewer side effects such as pain and bleeding (Bingham et al, 2001a; Goldfrank, 1998; HSDB, 2002).
    7) Copper and its compounds have many other miscellaneous uses:
    a) They are used for chemical and pharmaceutical applications; in pollution control catalysts; in pigments, dyes and anti-fouling paints; in works of art; in coinage; in fabrics and textiles, glass and ceramics; in cement, nylon and paper products; for printing and photocopying; in pyrotechnics; as analytical reagents; and in wood preservatives.
    b) They are also used in ammunition, flameproofing and fuel additives, and the flakes are used as insulation for liquid fuels (ACGIH, 1996a; Budavari, 2000; HSDB, 2002; ILO, 1998; Lewis, 1997a).
    c) Copper naphthenate has been used as a coating material for hardwood floors, causing toxicity to residents (Kim & Chomchai, 1999).
    8) COPPER COMPOUNDS (Copper I and Copper II compounds):
    a) COPPER OXIDE: Cupric oxide (black copper oxide) (CuO) or Cuprous oxide (red copper oxide) (Cu2O). Copper oxide is used as a catalyst and a pigment for ceramic, glass, enamel, porcelain and artificial; it is used in copper metallurgy, pyrotechnics and welding and in the manufacture of rayon; it serves as a solvent for chromic iron ores; it is used as an optical glass polishing agent; and it is found in batteries, electrodes, desulfurizing oils, paints fungicides and insecticides (Bingham et al, 2001; Budavari, 2000; ILO, 1998).
    b) COPPER ACETATE: Cupric acetate or cupric acetate, basic or Cuprous acetate (acetic acid copper (1+) salt). Copper acetate is used as a paint pigment, insecticide, fungicide, mordant and mildew preventive (Budavari, 2000).
    c) COPPER CARBONATE: Cupric carbonate, basic (copper carbonate hydroxide). Copper carbonate is used in pigments, pyrotechnics, insecticides, fungicides and brass coloring (Clayton & Clayton, 1994).
    d) COPPER CHLORIDE: Cupric chloride (CuCl2) or Cuprous chloride (CuCl). Copper chloride is used as a disinfectant, in metallurgy, for the preservation of wood pulp, for deodorizing and desulfurizing petroleum distillates, in photography, in water purification, and as a feed additive (Clayton & Clayton, 1994).
    e) COPPER NITRATE: Cupric nitrate (CuN2O6). The nitrate shares many uses with copper chloride and, in addition, is used preferentially in pharmaceutical preparations and in paints, varnishes and enamels (Clayton & Clayton, 1994).
    f) COPPER CYANIDE: Cuprous cyanide (CuCN). Its chief use is in the electroplating of copper on iron (Clayton & Clayton, 1994).
    g) COPPER GLYCINATE - Copper glycinate is used in cattle to increase dairy yields (Oon et al, 2006).
    h) COPPER SULFATE/SULFIDE: Cupric sulfate, basic (copper hydroxide sulfate) or Cupric sulfide(CuS) or Cuprous sulfide (Cu2S). It is used as a fungicide, molluscicide and wood preservative, for water treatment as a bactericide and algaecide, as a mordant, in electroplating, as a froth flotation agent, in leather tanning and hide preservation, in works of art, for animal nutrition, and in some fertilizers. It is also used medicinally as an emetic, and in several intrauterine contraceptive devices (Bingham et al, 2001; ILO, 1998; Kirk-Othmer, 1992).

Life Support

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

Clinical Effects

    0.2.1) SUMMARY OF EXPOSURE
    A) WITH POISONING/EXPOSURE
    1) ROUTES OF EXPOSURE: Copper compounds may be toxic by inhalation, ingestion, injection, and skin or eye exposure. Copper salts are particularly irritating.
    2) INHALATION: Exposure to fumes or dust may cause irritation of the nose and upper respiratory tract, as well as sneezing and coughing. Perforation of the nasal septum can also occur. 'Metal fume fever,' with respiratory and flu-like symptoms such as chills and muscle aches, may result from exposure to fumes or fine dust. The incidence of copper-induced metal fume fever is low due to the high temperatures required to volatilize copper.
    3) INGESTION: Acute ingestion of copper salts can cause irritation, severe nausea and vomiting, salivation, abdominal pain, epigastric burning, hemolysis, gastrointestinal bleeding with hemorrhagic gastritis, hematemesis and melena, anemia, hypotension, jaundice, seizures, coma, shock and death. Hepatic and renal failure may develop several days after acute ingestion. Methemoglobinemia may rarely occur. Copper may produce a metallic or sweet taste.
    4) INJECTION: Subcutaneous injection of copper glycinate resulted in nausea and vomiting, acute renal failure, hemolytic anemia, acute hepatic failure, disseminated intravascular coagulation, and dermal necrosis at the injection site.
    5) DERMAL: Skin exposure may cause irritation, itching, eczema, allergic contact dermatitis, hypersensitivity, and a greenish discoloration of the hair, teeth and skin.
    6) EYE: Exposure of the eyes to copper fumes or dust can cause irritation, conjunctivitis, palpebral edema, ulceration and corneal turbidity. Eye irritation, uveitis, abscess and loss of the eye may also occur from the mechanical action of lodged copper particles. Penetration of the eye by fine fragments can result in severe ocular damage. Corneal discoloration (Kayser-Fleischer ring) is a hallmark of Wilson disease.
    0.2.3) VITAL SIGNS
    A) WITH POISONING/EXPOSURE
    1) Increased temperature may be noted in some cases.
    2) Hypotension may occur.
    3) Tachycardia and tachypnea have been reported following oral exposure to copper oxychloride.
    0.2.4) HEENT
    A) WITH POISONING/EXPOSURE
    1) Eye exposure may produce irritation, conjunctivitis, palpebral edema, ulceration and corneal turbidity. Eye irritation, uveitis, abscess and loss of the eye may result from severe mechanical irritation.
    0.2.5) CARDIOVASCULAR
    A) WITH POISONING/EXPOSURE
    1) Hypotension, dysrhythmia and coronary artery disease have been linked with exposure to copper.
    0.2.6) RESPIRATORY
    A) WITH POISONING/EXPOSURE
    1) Metal fume fever, wheezing and rales have been reported in workers exposed to fine copper dust. Dyspnea and tachypnea have developed after oral copper exposure. Pulmonary edema and alveolar inflammation have been noted in animals.
    0.2.7) NEUROLOGIC
    A) WITH POISONING/EXPOSURE
    1) Central nervous system depression, seizures and headaches have been associated with copper exposure.
    0.2.8) GASTROINTESTINAL
    A) WITH POISONING/EXPOSURE
    1) Gastroenteritis with vomiting may occur after ingestion of some copper salts. Mucosal erosions, a metallic taste, burning epigastric sensation and diarrhea may also occur.
    0.2.9) HEPATIC
    A) WITH POISONING/EXPOSURE
    1) Hepatomegaly, liver tenderness, increased levels of transaminase and jaundice may occur on the second or third day after ingestion of copper salts. Childhood cirrhosis has been linked with ingestion of milk from copper or brass drinking vessels. Granulomas have also been associated with copper exposure.
    0.2.10) GENITOURINARY
    A) WITH POISONING/EXPOSURE
    1) Acute renal failure with oliguria followed by anuria may occur 24 to 48 hours after ingestion. Hemoglobinuria and hematuria may also occur.
    0.2.13) HEMATOLOGIC
    A) WITH POISONING/EXPOSURE
    1) Hemolysis and anemia have occurred and, rarely, methemoglobinemia.
    0.2.14) DERMATOLOGIC
    A) WITH POISONING/EXPOSURE
    1) Skin exposure can produce in severe irritation, itching, erythema, dermatitis and eczema; systemic toxicity may result.
    0.2.21) CARCINOGENICITY
    A) Increased deaths from cancers have been linked to exposure to copper, mixed with other exposures. However, copper is considered not classifiable as to human carcinogenicity.

Laboratory Monitoring

    A) Obtain whole blood copper levels if symptomatic.
    B) Obtain baseline liver function tests, renal function tests and CBC.

Treatment Overview

    0.4.2) ORAL/PARENTERAL EXPOSURE
    A) DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting.
    B) Vomiting is rapid and spontaneous in most patients following ingestion of copper salts.
    C) Copper salts may be caustic agents, capable of extensive mucosal damage, including perforation of the gastrointestinal tract. Gastric lavage and administration of charcoal may cause further complications. However, some clinicians have successfully utilized these techniques. Once charcoal is given, it is difficult to observe endoscopy findings. These are controversial techniques, and are left to the final judgement of the treating physician.
    1) Gastric lavage may be indicated after ingestion of non-corrosive forms of copper. Following ingestion of a corrosive copper compound, such as copper sulfate (cupric sulfate), gastric lavage is not indicated because the risk of causing perforation may outweigh the potential benefit of removing caustic material.
    2) GASTRIC LAVAGE: Consider after ingestion of a potentially life-threatening amount of poison if it can be performed soon after ingestion (generally within 1 hour). Protect airway by placement in the head down left lateral decubitus position or by endotracheal intubation. Control any seizures first.
    a) CONTRAINDICATIONS: Loss of airway protective reflexes or decreased level of consciousness in unintubated patients; following ingestion of corrosives; hydrocarbons (high aspiration potential); patients at risk of hemorrhage or gastrointestinal perforation; and trivial or non-toxic ingestion.
    D) HYPOTENSION: Infuse 10 to 20 mL/kg isotonic fluid. If hypotension persists, administer dopamine (5 to 20 mcg/kg/min) or norepinephrine (ADULT: begin infusion at 0.5 to 1 mcg/min; CHILD: begin infusion at 0.1 mcg/kg/min); titrate to desired response.
    E) Keep patients who have ingested corrosive copper salts NPO following mucosal decontamination until after endoscopy consultation.
    F) Consider endoscopy in patients who have ingested corrosive copper salts.
    1) ENDOSCOPY: Early endoscopy allows patients without gastrointestinal injury to be medically cleared, and provides important prognostic information in patients who do have varying degrees of gastrointestinal burns. In addition, it facilitates the safe placement of enteral feeding tubes thereby shortening the period of time that patients with burns are without enteral nutritional support. Endoscopy should be performed within the first 24 hours post-ingestion, and should be avoided from 2 days to 2 weeks post-ingestion since wound tensile strength is lowest and the risk of perforation highest during this time. Endoscopy is indicated for all adults with deliberate ingestion or any signs or symptoms attributable to ingestion, and for children with stridor, vomiting, or drooling. Consider endoscopy in children with dysphagia, refusal to swallow, significant oral burns, or abdominal pain. If second or third degree burns are found, follow 10 to 20 days later with barium swallow or esophagram.
    G) The role of corticosteroids is controversial. Consider use in second-degree burns no more than 48 hours postingestion in patients without active upper gastrointestinal bleeding or evidence of gastroesophageal rupture. Antibiotics are indicated for definite infection or patients with gastroesophageal perforation.
    H) SURGICAL OPTIONS: Initially, if severe esophageal burns are found a string may be placed in the stomach to facilitate later dilation. Insertion of a specialized nasogastric tube after confirmation of a circumferential burn may prevent strictures. Dilation is indicated after 2 to 4 weeks if strictures are confirmed; if unsuccessful, either colonic intraposition or gastric tube placement may be performed. Consider early laparotomy in patients with severe esophageal and/or gastric burns.
    I) There is little clinical experience in the use of chelators in the setting of acute copper intoxication. Data on efficacy is derived from patients with chronic copper intoxication (Wilson disease, Indian childhood cirrhosis) and animal studies. BAL, penicillamine, DMPS and EDTA have been used. D-penicillamine is considered the drug of choice for Wilson disease, a condition of chronic copper overload.
    1) D-PENICILLAMINE: Use only if less toxic agents not available or not tolerated. USUAL DOSE: ADULT: 1 to 1.5 g/day given orally in 4 divided doses. CHILD: 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). Avoid if penicillin allergic. Monitor for proteinuria, hematuria, rash, leukopenia, thrombocytopenia.
    2) Administer BAL (Dimercaprol) 3 to 5 mg/kg/dose IM every 4 hours for 2 days; then every 4 to 6 hours for an additional 2 days; then every 4 to 12 hours for up to 7 additional days.
    J) METHEMOGLOBINEMIA: Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy.
    K) METHYLENE BLUE: INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules and 10 mg/1 mL (1% solution) vials. Additional doses may sometimes be required. Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection. NEONATES: DOSE: 0.3 to 1 mg/kg.
    L) Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome.

Range Of Toxicity

    A) Severe intoxication is associated with serum copper levels greater than 500 mcg/dL. The estimated lethal dose in an untreated adult is 10 to 20 g copper.

Summary Of Exposure

    A) WITH POISONING/EXPOSURE
    1) ROUTES OF EXPOSURE: Copper compounds may be toxic by inhalation, ingestion, injection, and skin or eye exposure. Copper salts are particularly irritating.
    2) INHALATION: Exposure to fumes or dust may cause irritation of the nose and upper respiratory tract, as well as sneezing and coughing. Perforation of the nasal septum can also occur. 'Metal fume fever,' with respiratory and flu-like symptoms such as chills and muscle aches, may result from exposure to fumes or fine dust. The incidence of copper-induced metal fume fever is low due to the high temperatures required to volatilize copper.
    3) INGESTION: Acute ingestion of copper salts can cause irritation, severe nausea and vomiting, salivation, abdominal pain, epigastric burning, hemolysis, gastrointestinal bleeding with hemorrhagic gastritis, hematemesis and melena, anemia, hypotension, jaundice, seizures, coma, shock and death. Hepatic and renal failure may develop several days after acute ingestion. Methemoglobinemia may rarely occur. Copper may produce a metallic or sweet taste.
    4) INJECTION: Subcutaneous injection of copper glycinate resulted in nausea and vomiting, acute renal failure, hemolytic anemia, acute hepatic failure, disseminated intravascular coagulation, and dermal necrosis at the injection site.
    5) DERMAL: Skin exposure may cause irritation, itching, eczema, allergic contact dermatitis, hypersensitivity, and a greenish discoloration of the hair, teeth and skin.
    6) EYE: Exposure of the eyes to copper fumes or dust can cause irritation, conjunctivitis, palpebral edema, ulceration and corneal turbidity. Eye irritation, uveitis, abscess and loss of the eye may also occur from the mechanical action of lodged copper particles. Penetration of the eye by fine fragments can result in severe ocular damage. Corneal discoloration (Kayser-Fleischer ring) is a hallmark of Wilson disease.

Vital Signs

    3.3.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Increased temperature may be noted in some cases.
    2) Hypotension may occur.
    3) Tachycardia and tachypnea have been reported following oral exposure to copper oxychloride.
    3.3.2) RESPIRATIONS
    A) WITH POISONING/EXPOSURE
    1) TACHYPNEA has been reported following acute and chronic oral exposure to copper oxychloride (Gunay et al, 2006).
    3.3.3) TEMPERATURE
    A) WITH POISONING/EXPOSURE
    1) FEVER has been reported with copper sulfate intoxication and might develop after ingestion of other copper salts (Akintonwa et al, 1989).
    3.3.4) BLOOD PRESSURE
    A) WITH POISONING/EXPOSURE
    1) HYPOTENSION has been reported with severe copper sulfate poisoning and might develop after ingestion of other copper salts (Chuttani et al, 1965; Agarwal et al, 1993).
    3.3.5) PULSE
    A) WITH POISONING/EXPOSURE
    1) TACHYCARDIA has been reported following acute and chronic oral exposure to copper oxychloride (Gunay et al, 2006).

Heent

    3.4.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Eye exposure may produce irritation, conjunctivitis, palpebral edema, ulceration and corneal turbidity. Eye irritation, uveitis, abscess and loss of the eye may result from severe mechanical irritation.
    3.4.3) EYES
    A) WITH POISONING/EXPOSURE
    1) CONJUNCTIVITIS: Exposure to copper can result in conjunctivitis and corneal ulceration or turbidity as well as palpebral edema (ACGIH, 1996; Goldfrank, 1998; Sittig, 1991).
    2) IRRITATION: Transient irritation of the eyes occurred after exposure to a fine dust of oxidation products of copper produced in an electric arc (Hathaway et al, 1996). Copper chloride produced severe eye irritation and permanent corneal opacifications in rabbits (Grant & Schuman, 1993).
    3) BURN: The strong alkalinity of copper cyanide solutions used in plating baths can result in severe eye burns with corneal damage (Grant & Schuman, 1993).
    4) CHALCOSIS LENTIS: Copper or copper alloy foreign bodies lodged in the eye (chalcosis lentis) can result in uveitis, abscess, serious injury or loss of the eye; over time, the copper may dissolve and disseminate to the lens, cornea and iris, where it may produce a greenish-brown discoloration of the anterior capsule visible by slit-lamp microscope (Goldfrank, 1998; Grant & Schuman, 1993).
    5) Retinal injury has been reported as a result of the intra-ocular retention of a copper foreign body. Electro-retinographic changes improved, but did not fully reverse, following removal of the object (Dayan et al, 1999).
    6) Several outbreaks of severe corneal injury were reported after the introduction of plasma gas sterilization techniques. The injury is believed to be due to copper and/or zinc residues on the surface of the instruments (Duffy et al, 2000; Smith et al, 2000).
    7) WILSON DISEASE: Discoloration of the peripheral parts of the corneas (Kayser-Fleischer rings) is a non-injurious hallmark feature of Wilson disease, a hereditary metabolic disorder characterized by deposition of copper in parenchymal tissue. A 'sunflower-like' discoloration of the most anterior layers of the lens has also been reported in patients with Wilson disease (Baselt, 2000; Grant & Schuman, 1993).
    3.4.5) NOSE
    A) WITH POISONING/EXPOSURE
    1) IRRITATION: Nasal mucous membranes may become irritated after inhalation exposure to the dusts and mists of copper salts; ulceration and perforation of the nasal septum may result in some cases, with atrophic changes of the nasal mucous membranes (ACGIH, 1996; Sittig, 1991).
    3.4.6) THROAT
    A) WITH POISONING/EXPOSURE
    1) METALLIC TASTE: Acute systemic intoxication may produce a metallic or sweet taste in the mouth (ACGIH, 1996; Burnett, 1989).
    2) ORAL FIBROSIS: Oral submucous fibrosis has been reported rarely (0.05% incidence) in areca-nut chewers. It has been suggested that copper may be involved in the pathogenesis of this disorder, although this has not been adequately substantiated (Meghji et al, 1997).
    3) CASE REPORT: Pharyngeal erythema with mild dysphagia was reported in an 89-year-old woman following a suspected ingestion of an algaecide containing copper ethanolamine complex (Graham et al, 2015).

Cardiovascular

    3.5.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Hypotension, dysrhythmia and coronary artery disease have been linked with exposure to copper.
    3.5.2) CLINICAL EFFECTS
    A) HYPOTENSIVE EPISODE
    1) WITH POISONING/EXPOSURE
    a) Hypotension has been noted after acute ingestion of copper sulfate and might develop after ingestion of other copper salts (Stein et al, 1976; Chugh et al, 1977; Schwartz & Schmidt, 1986).
    B) CONDUCTION DISORDER OF THE HEART
    1) WITH POISONING/EXPOSURE
    a) In a nested case-control study within a prospective population study, cardiovascular mortality was found to be significantly increased in a population of patients with high serum copper and low serum zinc levels (Reunanen et al, 1996).
    b) Tachycardia has been reported following acute and chronic oral exposure to copper oxychloride (Gunay et al, 2006).
    C) DISORDER OF CORONARY ARTERY
    1) WITH POISONING/EXPOSURE
    a) Limited epidemiologic data indicate that coronary heart disease is associated with modest (5%) increases in serum copper. It is not apparent whether copper is a cause of heart disease or simply serves as a marker of some other phenomenon (Ford, 2000).
    b) Additional epidemiologic studies of copper and heart disease have been reviewed and do not provide convincing evidence of a causal relationship (Anon, 1998).

Respiratory

    3.6.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Metal fume fever, wheezing and rales have been reported in workers exposed to fine copper dust. Dyspnea and tachypnea have developed after oral copper exposure. Pulmonary edema and alveolar inflammation have been noted in animals.
    3.6.2) CLINICAL EFFECTS
    A) METAL FEVER
    1) WITH POISONING/EXPOSURE
    a) Metal fume fever has been reported in workers exposed to an extremely fine copper dust at concentrations of 0.075 to 0.12 mg/m(3) (Proctor & Hughes, 1978). Symptoms include upper respiratory irritation, chills and muscle aches (Baselt, 2000).
    b) Some authors have questioned this association (Borak et al, 2000).
    B) BRONCHOSPASM
    1) WITH POISONING/EXPOSURE
    a) Wheezing and rales on auscultation were reported in eight patients exposed to fumes while cutting brass pipes. Increased urine copper levels were noted (Armstrong et al, 1983).
    C) DISORDER OF RESPIRATORY SYSTEM
    1) WITH POISONING/EXPOSURE
    a) DYSPNEA: 40-year-old man developed methemoglobinemia, cyanosis and dyspnea approximately 5 hours after ingestion of a fungicide containing copper 8-hydroxyquinolate (Yang et al, 1997).
    b) TACHYPNEA has been reported following acute and chronic oral exposure to copper oxychloride (Gunay et al, 2006).
    c) LACK OF INFORMATION
    1) Lung damage after chronic exposure to fumes in industry has not been described. The higher incidence of respiratory cancer reported in copper smelters has been attributed to the presence of arsenic in the ore (Hathaway et al, 1996).
    3.6.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) PULMONARY EDEMA
    a) Pulmonary edema has been reported in dogs following exposures to copper acetate dusts (Brodskii, 1933).
    2) RESPIRATORY DISORDER
    a) INFLAMMATION: Chronic inhalation of copper-containing aerosols has caused pulmonary alveolar proteinosis in rats (Likhaechev et al, 1975).

Neurologic

    3.7.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Central nervous system depression, seizures and headaches have been associated with copper exposure.
    3.7.2) CLINICAL EFFECTS
    A) CENTRAL NERVOUS SYSTEM DEFICIT
    1) WITH POISONING/EXPOSURE
    a) Lethargy and coma have been reported in patients with severe copper sulfate intoxication and might develop after ingestion of other copper salts (Schwartz & Schmidt, 1986; Agarwal et al, 1993).
    B) SEIZURE
    1) WITH POISONING/EXPOSURE
    a) Copper is reportedly linked with toxin-induced seizures (Goldfrank, 1998).
    C) HEADACHE
    1) WITH POISONING/EXPOSURE
    a) Headache, vomiting and abdominal pain immediately developed in an adult after ingestion of two mouthfuls of a fungicide containing copper 8-hydroxyquinolate; methemoglobinemia with hemolysis developed later (Yang et al, 1997).
    D) PARKINSON'S DISEASE
    1) WITH POISONING/EXPOSURE
    a) Limited epidemiologic evidence associates the development of Parkinson disease with occupational exposure to copper in excess of 20 years. Possible interactions with lead, iron and manganese have been suggested (Gorell et al, 1999).

Gastrointestinal

    3.8.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Gastroenteritis with vomiting may occur after ingestion of some copper salts. Mucosal erosions, a metallic taste, burning epigastric sensation and diarrhea may also occur.
    3.8.2) CLINICAL EFFECTS
    A) GASTROENTERITIS
    1) WITH POISONING/EXPOSURE
    a) The irritant effects of ingestion of sufficient concentrations of copper salts may include a metallic taste, salivation, nausea, vomiting, burning in the epigastrium, abdominal/gastric pain and bloody diarrhea. Copper sulfate has been reported to cause gastrointestinal bleeding (hemorrhagic gastritis), which may potentially occur with other irritating copper salts (ACGIH, 1996; Agarwal et al, 1975; ILO , 1998) Jantsch et al, 1984; (Sittig, 1991; Yang et al, 1997).
    b) Copper salts may induce a rapid onset of repeated vomiting (98% within 15 minutes of ingestion), with a range of two to ten episodes of vomiting following a single oral dose. The vomitus is characteristically greenish-blue (Gulliver, 1991; Gunay et al, 2006). The emetic effect seems to be secondary to the irritant effects of copper.
    c) Reported cases of acute gastrointestinal 'upset' due to copper have been reviewed, and diagnostic criteria proposed (Eife et al, 1999a; Eife et al, 1999b). Acute gastrointestinal symptoms have occurred as a result of several incidents in which new copper piping was installed to supply domestic water (Knobeloch et al, 1998).
    d) An outbreak of gastroenteritis occurred after the leaching of copper into drinking water as a result of carbon dioxide gas, which lowered the pH of the water. The water had a strong metallic taste (Witherell et al, 1980). Another outbreak was reported in several children who drank an acidic lime cordial from a copper urn; the beverage was found to have a copper concentration of 300 mg/L (Gill & Bhagat, 1999).
    e) CASE SERIES: In a cluster of cases, an outbreak of abdominal pain, vomiting and complaint of metallic taste occurred on a small industrial estate in the United Kingdom in which copper was present in the water supply system (water was obtained from two boreholes and chlorinated by salt electrolysis before distribution). Of note, the only workers who became ill typically consumed only bottled water; those that did ingest the tap water regularly did not become ill. Prior to this outbreak, many individuals had stopped consuming the tap water because of a "bad taste". The authors suggested that people who were regularly exposed to high concentrations of copper may have become tolerant. Copper levels dropped after water was received from a public water supply (Hoveyda et al, 2003).
    f) CASE REPORT (PEDIATRIC): A 2-year-old-boy experienced abdominal pain and vomiting within a few hours, and bright-green-colored stools within 48 hours of ingestion of a blue ballpoint pen refill containing copper phthalocyanines (Forrester, 1975).
    g) CASE REPORT (PEDIATRIC): Three cases of children with protracted diarrhea after exposure to copper in domestic water were reported. The symptoms resolved on withdrawal and reappeared on re-institution of domestic water use (Stenhammer, 1999).
    h) CASE REPORT (ADULT): A 40-year-old man immediately developed vomiting, abdominal pain and headache after ingestion of a fungicide containing copper 8-hydroxyquinolate. Diarrhea developed within five hours of the exposure (Yang et al, 1997).
    i) CASE REPORT: Nausea and vomiting were reported in a 41-year-old woman following intentional subcutaneous administration of copper glycinate (equivalent to 2.5 grams of copper) into 3 sites on her left forearm (Oon et al, 2006).
    j) CASE REPORT: An 89-year-old woman presented with vomiting, that was green in color, and diarrhea after a suspected ingestion of an algaecide containing copper ethanolamine complex. She also developed pharyngeal erythema with mild dysphagia, mixed hyperbilirubinemia, and pancreatitis. Laboratory data revealed elevated copper levels at 2002 mcg/dL (reference 70 to 175 mcg/dL). There was no evidence of hemolysis, significant hepatotoxicity, renal dysfunction, or methemoglobinemia. With supportive care, the patient's symptoms improved and she was discharged (Graham et al, 2015).

Hepatic

    3.9.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Hepatomegaly, liver tenderness, increased levels of transaminase and jaundice may occur on the second or third day after ingestion of copper salts. Childhood cirrhosis has been linked with ingestion of milk from copper or brass drinking vessels. Granulomas have also been associated with copper exposure.
    3.9.2) CLINICAL EFFECTS
    A) HEPATIC NECROSIS
    1) WITH POISONING/EXPOSURE
    a) Jaundice appears in about 25% of patients on the second or third day after acute ingestion of copper salts and may be accompanied by hepatomegaly, increased levels of transaminase and liver tenderness, with biopsy showing centrilobular necrosis and biliary stasis (Gunay et al, 2006; Baxter et al, 2000a; Zimmerman, 1978). Hepatic accumulation of copper is an essential feature of the development of copper toxicosis (Bremner, 1998).
    b) Hepatic necrosis was reported in a 46-year-old man after chronic ingestion of copper coins. Electron micrograph showed dense deposits of copper in the hepatocytes at autopsy (Hasan et al, 1995).
    B) CIRRHOSIS OF LIVER
    1) WITH POISONING/EXPOSURE
    a) CHILDHOOD CIRRHOSIS: Indian childhood cirrhosis has been associated with increased hepatic copper concentrations, partly attributable to the use of copper or brass drinking vessels used to prepare animal milk or water. Milk apparently takes up copper more readily than water does, and thus milk copper contamination may be the cause (Bhave et al, 1987; Horslen et al, 1994; O'Neill & Tanner, 1989; Tanner et al, 1983; Tanner, 1998).
    1) Multiple cases of childhood cirrhosis have been reported from various locations, but the involvement of copper in these cases is not entirely apparent (Rodec et al, 1999; (Walker, 1999; Walker-Smith, 1999) Trollman et al, 1999). The histological pattern of liver damage in a series of 12 German infants was noted to be variable (Muller-Hocker et al, 1998).
    2) Various authors have suggested that at least some of these cases may be due to an inherited disorder, an inherited predisposition in conjunction with increased copper intake, or the result of copper in conjunction with some other environmental factor(s) (Horslen et al, 1994; Scheinberg & Sternlieb, 1994; Tanner, 1998; Tanner, 1998; Muller et al, 1998; Anon, 1998).
    b) IDIOPATHIC COPPER TOXICOSIS is related to abnormal hepatic copper accumulation with cirrhosis and cholestasis, not always due to an exogenous copper source, and is characterized by distinct clinical and pathologic features.
    1) This disorder is generally found in such pediatric liver diseases as Wilson disease, Indian childhood cirrhosis, the non-Indian disease called idiopathic copper toxicosis, and disorders associated with chronic cholestasis (Muller et al, 1998). These diseases usually result from a genetic predisposition to the hepatic accumulation of copper (Barceloux, 1999; Anon, 1998).
    2) CASE REPORT: An adult consuming copper supplements for 3 years at doses of 30 to 60 mg per day developed cirrhosis necessitating liver transplantation (O'Donohue et al, 1999).
    C) HEPATIC FAILURE
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: Acute hepatic failure was reported in a 41-year-old woman approximately 4 days following intentional subcutaneous administration of copper glycinate (equivalent to 2.5 grams copper). Her ALT and AST levels peaked at 2903 Units/L and 6654 Units/L, respectively, 3 days after admission (Oon et al, 2006).
    b) CASE REPORT (CHILD): A 6-year-old boy presented with fatigue and abdominal distention that progressed over a period of several weeks. An abdominal ultrasound indicated hepatosplenomegaly and laboratory data revealed elevated liver enzymes (ALT 275 units/L, AST 707 units/L, GGT 155 units/L) and a total bilirubin of 1.2 mg/dL. Urine copper was slightly elevated at 212 mcg/L; however a penicillamine challenge test indicated a 24-hour urine copper of 1600 mcg/day. A liver biopsy showed extensive fibrosis and microscopic staining was positive for copper. The dry copper weight was 1400 mcg/g of liver tissue and, because there was no indication of copper exposure in his history, Wilson disease was suspected; however, genetic testing showed no mutations known to code for Wilson disease. Despite chelation therapy with trientene and zinc, acute liver failure occurred, with a bilirubin concentration of 50 mg/dL and an INR of 6. The patient received a liver transplant and recovered uneventfully. Further questioning of the patient's mother revealed that he had been receiving an energy drink mixed with chocolate milk on a daily basis for the previous 8 months, as well as 2 multivitamins daily. Total amount of copper consumed was 9088 mcg/day, approximately 21 times the recommended daily allowance for his age (Bartlett & Erickson, 2012).
    1) His fraternal twin brother, who also consumed the same amount of copper (9088 mcg/day for 8 months), developed mildly elevated ALT and AST concentrations; however, a liver biopsy was negative for fibrosis or inflammation. Microscopic staining was positive for copper and he had a dry copper weight of 3020 mcg/g of liver tissue. He remained stable following chelation therapy with penicillamine. It is suspected that the first patient may have had either underlying liver disease or a possible unidentified defect of copper metabolism, resulting in liver failure despite a dry copper weight of less than half that of his brother (Bartlett & Erickson, 2012).
    D) INJURY OF LIVER
    1) WITH POISONING/EXPOSURE
    a) Vineyard workers exposed to an antifungal spray containing copper sulfate developed liver granulomas with accompanying increased serum alkaline phosphate levels and hepatomegaly. Other effects of chronic exposure in these workers included Kupffer cell proliferation, fibrosis, cirrhosis and portal hypertension (Baxter et al, 2000a).
    E) HYPERBILIRUBINEMIA
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: Mixed hyperbilirubinemia (total 3.2 mg/dL, direct 1.1, indirect 2.2) occurred in an 89-year-old woman following a suspected ingestion of an algaecide containing copper ethanolamine complex. The patient also developed vomiting that was green in color, diarrhea, pancreatitis, and pharyngeal erythema with mild dysphagia. Laboratory data revealed elevated copper levels at 2002 mcg/dL (reference 70 to 175 mcg/dL). There was no evidence of hemolysis, significant hepatotoxicity, renal dysfunction, or methemoglobinemia. With supportive care, the patient's symptoms improved and she was discharged (Graham et al, 2015).
    3.9.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    1) HEPATIC CIRRHOSIS
    a) Animal studies suggested that pyrolizidine alkaloids secreted into milk by grazing animals may contribute to the development of Indian childhood cirrhosis (Morris et al, 1994). In rats, chronic ingestion of copper and retroserine increased hepatic injury and copper accumulation and decreased survival compared with chronic ingestion of copper or retroserine alone (Morris et al, 1994).

Genitourinary

    3.10.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Acute renal failure with oliguria followed by anuria may occur 24 to 48 hours after ingestion. Hemoglobinuria and hematuria may also occur.
    3.10.2) CLINICAL EFFECTS
    A) ACUTE RENAL FAILURE SYNDROME
    1) WITH POISONING/EXPOSURE
    a) Acute renal failure develops in 20% to 40% of patients with acute copper sulfate intoxication and is believed to be mainly due to intravascular hemolysis. This might also occur after ingestion of other copper salts. Anuria or oliguria may develop 24 to 48 hours after ingestion, accompanied by an increase in BUN (Wahl et al, 1963; Chugh et al, 1977; Chugh et al, 1977a).
    b) Acute tubular necrosis follows by several hours the acute gastrointestinal symptoms of copper salt ingestion (Baxter et al, 2000a).
    c) Biopsies showing swelling or necrosis of the tubular cells, glomerular congestion and occasional hemoglobin cast have been noted. Necrosis seems to be due to a direct toxicity to renal tubular cells, as many of these patients do not have severe hemolysis or hypotension (Dash, 1989).
    d) CASE REPORT: Acute renal failure with hemoglobinuria occurred in a 41-year-old woman following intentional subcutaneous administration of copper glycinate (equivalent to 2.5 grams of copper). At admission, her serum creatinine level was 0.249 mmol/L and her BUN was 13.9 mmol/L. Despite supportive care with fluids, chelation with d-penicillamine, and sodium thiosulfate administration, her renal failure progressed to anuria, requiring continuous veno-venous hemodiafiltration (CVVHDF) that continued intermittently over a 16-day period (a total of 394 hours). Three weeks after initial presentation, following discharge from the ICU, the patient continued to have severe renal insufficiency with a serum creatinine level of 0.590 mmol/L (Oon et al, 2006).
    e) CASE REPORT: Acute renal failure was reported in a 19-year-old man who intentionally ingested a glassful of liquid pesticide containing copper oxychloride. His urinary output was decreased and laboratory data revealed a serum creatinine of 13.2 mg/dL and an elevated urea concentration of 318 mg/dL. Urinalysis showed evidence of proteinuria (+4 protein) and hematuria (+3 red blood cells). Despite treatment with 5 hemodialysis sessions, the renal failure persisted and the patient was subsequently enrolled in a dialysis program (Gunay et al, 2006).
    B) BLOOD IN URINE
    1) WITH POISONING/EXPOSURE
    a) Hemoglobinuria and hematuria have been reported after copper sulfate ingestion and might occur with intoxication from other copper salts (Walsh et al, 1977).
    C) ABNORMAL URINE
    1) WITH POISONING/EXPOSURE
    a) Dark urine developed in a 40-year-old man within 5 hours of ingesting two mouthfuls of a fungicide containing copper 8-hydroxyquinolate (Yang et al, 1997).

Acid-Base

    3.11.2) CLINICAL EFFECTS
    A) ACIDOSIS
    1) WITH POISONING/EXPOSURE
    a) Metabolic acidosis has been described in patients with hemodialysis-induced copper toxicity (Klein et al, 1972; Eastwood et al, 1983).

Hematologic

    3.13.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Hemolysis and anemia have occurred and, rarely, methemoglobinemia.
    3.13.2) CLINICAL EFFECTS
    A) HEMOLYSIS
    1) WITH POISONING/EXPOSURE
    a) Intravascular red cell hemolysis has been reported after acute ingestion (Chugh et al, 1977; ILO , 1998; Walsh et al, 1977; Yang et al, 1997; Yang et al, 2004; Gunay et al, 2006). Hemolytic anemia may follow several hours after the acute gastrointestinal symptoms of copper salt ingestion (Baxter et al, 2000a).
    b) Severe hemolysis (lowest hemoglobin reported, 7.3 g/dL) requiring repeated blood transfusions occurred in a 40-year-old man after ingestion of two mouthfuls of a fungicide containing copper 8-hydroxyquinolate. The patient was also treated for persistent methemoglobinemia (Yang et al, 1997; Yang et al, 2004).
    c) CASE REPORT: A 41-year-old woman developed acute hemolytic anemia (lowest hemoglobin reported, 58 g/L) requiring several blood transfusions over a two-week period, totalling 11 units of packed cells, after intentionally injecting herself subcutaneously with copper glycinate (equivalent to 2.5 grams of copper). The patient also developed a coagulopathy requiring treatment with fresh-frozen plasma and cryoprecipitate (Oon et al, 2006).
    B) METHEMOGLOBINEMIA
    1) WITH POISONING/EXPOSURE
    a) Rarely, methemoglobinemia has been reported (Chugh et al, 1975; Eastwood et al, 1983; Kim & Chomchai, 1999; Matter et al, 1969; Todd & Thompson, 1961; Yang et al, 1997; Yang et al, 2004).
    b) CASE REPORT (INFANT): A case was reported of a 6-week-old infant with methemoglobinemia due to well water with a high copper and nitrate content. Nitrates in well water are well-established inducers of methemoglobin, especially in susceptible populations such as infants. It is likely that nitrates contributed more than copper to the methemoglobinemia in this case (MMWR, 1993).
    c) CASE REPORT: Methemoglobinemia (24%) and hemolysis were reported in a 40-year-old man after ingestion of two mouthfuls of a fungicide containing copper 8-hydroxyquinolate. It was suggested that methylene blue was only partially effective in decreasing the methemoglobinemia level (20.7%) due to the fungicide's ability to inhibit G6PD activity.
    1) BAL and plasma exchange therapy were also initiated and the methemoglobin level dropped to 1.1%. The patient recovered without sequelae (Yang et al, 1997; Yang et al, 2004).
    d) CASE REPORT: Increased methemoglobin levels and serum copper levels were reported in a 40-year-old woman after residential exposure to copper naphthenate after a heavy spraying onto a hardwood floor with spillage of the container into a crawl space. Three months after continuous exposure, her methemoglobin level was 16%, which decreased to 0.9% 12 days after removal from the copper source. Naphthenic acid may have contributed to the methemoglobinemia (Kim & Chomchai, 1999).
    C) ANEMIA
    1) WITH POISONING/EXPOSURE
    a) CHRONIC: Chronic exposure to copper may produce anemia (ACGIH, 1996). Normocytic normochromic anemia (hemoglobin level ranging from 8.7 to 10.4 g/dL) was reported in 4 patients following chronic exposure to a pesticide containing copper oxychloride (Gunay et al, 2006).

Dermatologic

    3.14.1) SUMMARY
    A) WITH POISONING/EXPOSURE
    1) Skin exposure can produce in severe irritation, itching, erythema, dermatitis and eczema; systemic toxicity may result.
    3.14.2) CLINICAL EFFECTS
    A) DERMATITIS
    1) WITH POISONING/EXPOSURE
    a) Skin contact with some copper salts may result in severe irritation, with itching, erythema and dermatitis, and may produce systemic toxicity (Holzman et al, 1966).
    B) CONTACT DERMATITIS
    1) WITH POISONING/EXPOSURE
    a) Six cases of allergic contact dermatitis have been reported in the world literature up to 1972: three involved contact with industrial exposure to brass (2 Cu; 1 Zn); one case was a worker who transported sacks of CuSO4; another, a telephone wire man exposed to copper; and the sixth worker exposed to various pieces of copper-containing jewelry (Clayton & Clayton, 1981).
    b) Peri-menstrual recurrence of contact dermatitis has been reported in a patient using a copper-containing intrauterine device (Pujol et al, 1998).
    C) ECZEMA
    1) WITH POISONING/EXPOSURE
    a) The irritating effects of copper salts on the skin result in itching eczema (ACGIH, 1996).
    D) PUNCTURE WOUND - INJURY
    1) WITH POISONING/EXPOSURE
    a) CASE REPORT: A 27-year-old agricultural worker inadvertently injected his left lower leg with 120 mg (2 mL) of a copper glycinate cattle veterinary solution. At the injection site a 3 x 3 cm central dark necrotic area developed along with a 10 cm area of erythema and edema. Skin debridement showed evidence of extensive blackish-grey discoloration of the skin, subcutaneous fat and deep fascia, which were all necrotic. Serum copper level drawn the next day after the injury was not elevated. Treatment included split skin grafting that needed to be partially redone due to a staph aureus infection and poor adherence of the graft. Healing was noted at approximately 11 weeks. However, the patient remained symptomatic with persistent neurogenic pain (Atkinson et al, 2004).
    b) CASE REPORT: Dermal necrosis at the injection site occurred in a 41-year-old woman following intentional subcutaneous administration of copper glycinate (equivalent to 2.5 grams of copper) at 3 different sites on her left forearm. The patient required extensive debridement and split-skin grafting (Oon et al, 2006).
    E) HAIR DISCOLORATION
    1) WITH POISONING/EXPOSURE
    a) Very high levels of exposure to copper dust or fume may result in symptomless greenish discoloration of the hair, tongue and teeth (ACGIH, 1996; Baxter et al, 2000a; Hathaway et al, 1991).
    b) GREEN HAIR: Green pigmentation of blonde hair has been reported after exposure to copper-contaminated tap water, swimming pools containing copper-based algicides and application of copper contaminated henna (Mascaro et al, 1995; Person, 1985; Tosti et al, 1991).

Reproductive

    3.20.2) TERATOGENICITY
    A) FETAL DISTRESS
    1) Fetuses of women with Wilson disease, a disorder of copper metabolism involving high serum copper levels, are at risk for intrauterine growth retardation (Chin, 1991; DuPont et al, 1991).
    B) ANIMAL STUDIES
    1) Copper salts were not found to be teratogenic to laboratory animals in some studies (Schardein, 2000). Copper was not teratogenic in hamsters (HSDB). The results of teratogenicity studies in rats, however, have been conflicting (RTECS , 2002; Giavini, 1980).
    2) In rats, copper was found to affect female fertility index and pre- and post-implantation mortality; it also produced fetotoxicity and developmental abnormalities of the central nervous system and musculoskeletal system (RTECS , 2002).
    3) Metallic copper was lethal to mouse and rat embryos (Brinser & Cross, 1972; Webb, 1973). Copper sulfate and citrate were teratogenic when injected in hamsters (Ferm & Hanlon, 1974). Copper may have been toxic to the embryos of rats when inhaled and to mice when given orally (Baghramian, 1975).
    4) Although excess copper may be harmful to reproduction, so also is copper DEFICIENCY. Copper deficiency produced positive results for teratogenicity in rats, pigs, sheep, guinea pigs and horses; mainly limb abnormalities or polymorphic defects resulted (Bennetts & Chapman, 1937; Everson & Wang, 1967; O'Dell, 1961; Schardein, 2000). A copper-deficient diet did not produce skeletal abnormalities in rats, however (Jankowski et al, 1993).
    3.20.3) EFFECTS IN PREGNANCY
    A) ABORTION
    1) A possible link between occupational exposure to copper and miscarriages in women working in the metallurgy industry in Finland with mixed exposures has been reported (Hemminki, 1980; Hemminki, 1983).
    2) One woman with Wilson disease had eight spontaneous abortions before having a normal gestation and delivery after receiving zinc sulfate treatment (Schagen van Leeuwen & Christiaens, 1991).
    B) PLACENTAL BARRIER
    1) Copper levels correlated with levels of cadmium and zinc in the placentas of 292 low-risk (multiparous) women (Kuhnert et al, 1993). Iron-folate supplementation beginning in the second trimester resulted in lower serum copper levels late in pregnancy (Burns & Patterson, 1993).
    2) Copper from intrauterine devices is available to the fetus, but fetal blood levels were lower than maternal levels, although fetal liver levels were higher (Creason, 1976; Friberg, 1986). Fetal cord blood copper levels averaged 35 percent of those in maternal blood; the latter averaged 135.3 (+/- 26.26) mcg/dL and were higher than levels found in nonpregnant women (Veena et al, 1991).
    C) LACK OF EFFECT
    1) Serum copper levels in pre-eclamptic pregnant women were not significantly different from those in women with normal pregnancies (Kisters et al, 1993).
    2) No differences in levels of serum copper and ceruloplasmin were found in pregnant women with gestational diabetes. Copper-zinc (CuZn) superoxide dismutase activity was significantly increased, but this response to oxidative stress was evidently not due to a deficiency of copper (Loven et al, 1992).
    D) ANIMAL STUDIES
    1) Copper was a possible cause of abortions in sheep (James, 1966).

Carcinogenicity

    3.21.1) IARC CATEGORY
    A) IARC Carcinogenicity Ratings for CAS7440-50-8 (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) Not Listed
    3.21.2) SUMMARY/HUMAN
    A) Increased deaths from cancers have been linked to exposure to copper, mixed with other exposures. However, copper is considered not classifiable as to human carcinogenicity.
    3.21.3) HUMAN STUDIES
    A) LACK OF INFORMATION
    1) Copper is classified by IRIS as D (not classifiable as to human carcinogenicity), based on a lack of human human data, inadequate animal data from assays of copper compounds, and equivocal mutagenicity data (HSDB , 2002).
    B) CARCINOMA
    1) Several epidemiological studies have reported increased deaths from various cancers in copper miners (Enterline & Marsh, 1982), in persons living near a copper smelter (Cordier, 1983), and in copper and zinc refiners (Logue, 1982), but these have all involved mixed exposures with other metals.
    2) Chinese copper miners (7088) exposed from 1969 to 1988 had an increased risk of mortality from lung cancer, related to duration of exposure and time since first exposure (Chen et al, 1993).
    3) Plasma copper concentrations were slightly but significantly higher in women diagnosed with breast cancer than in controls. Levels were 1.31 mg/L in breast cancer cases and 1.26 mg/L in controls who had been in a prospective breast cancer study for an average of 11 years (Overvad et al, 1993).
    3.21.4) ANIMAL STUDIES
    A) NEOPLASM
    1) According to the WHO review (Anon, 1998), "The available studies of the carcinogenicity studies of copper compounds in rats and mice have given no indication that copper salts are carcinogenic." However, the studies are noted to be inadequate in many cases.
    2) When implanted intrapleurally in rats, copper was found to be an equivocal tumorigenic agent in the respiratory system (RTECS , 2002).

Genotoxicity

    A) Mutagenic data for copper and its salts have been equivocal.

Monitoring Parameters Levels

    4.1.1) SUMMARY
    A) Obtain whole blood copper levels if symptomatic.
    B) Obtain baseline liver function tests, renal function tests and CBC.
    4.1.2) SERUM/BLOOD
    A) BLOOD/SERUM CHEMISTRY
    1) Acute whole blood copper levels should be obtained.
    a) Serum copper concentrations normally range from 10.5 to 23 micromoles/Liter (Bentur et al, 1988). Average levels are 1.09 mg/L for men, 1.20 mg/L for non-pregnant women and 2.39 mg/L for pregnant women (Baselt, 2000).
    b) Serum copper levels rise with age in men. Mean levels by age 80 were 1.3 mcg/mL, compared with 1.05 mcg/mL in 20-year-old men (Madaric et al, 1994).
    c) In packed red blood cells, erythrocyte copper levels are around 0.89 mg/L (Baselt, 2000).
    2) Baseline liver function tests and renal function tests should be obtained and followed daily until symptoms abate.
    B) HEMATOLOGIC
    1) Obtain hematologic evaluation and monitor methemoglobin levels in cyanotic patients.
    4.1.3) URINE
    A) URINARY LEVELS
    1) Normal daily excretion of copper in the urine is less than 0.6 micromole/day (Bentur et al, 1988).
    4.1.4) OTHER
    A) OTHER
    1) Electroretinograms are useful in detecting and following damage to the retina by intraocular copper. Abnormal ERG results indicate serious injury may be imminent and the copper should be removed. Analysis of aqueous humor by chemical assay and atomic absorption spectrophotometry has also been used as an early warning measure (Grant & Schuman, 1993).

Radiographic Studies

    A) RADIOGRAPHIC-OTHER
    1) Metallic copper is radiopaque (Bentur et al, 1988). X-rays may be useful to establish diagnosis. Copper salts are not considered radiopaque.

Methods

    A) SPECTROSCOPY/SPECTROMETRY
    1) Copper determinations can be done by atomic absorption spectrophometry (Bentur et al, 1988). Flame and flameless atomic absorption procedures are used for serum and urine samples (Baselt, 2000).
    B) COLORIMETRIC
    1) A colorimetric procedure using bathocuproine sulfonate is used to measure copper levels in protein-free filtrates of biological samples (Baselt, 2000).

Life Support

    A) Support respiratory and cardiovascular function.

Monitoring

    A) Obtain whole blood copper levels if symptomatic.
    B) Obtain baseline liver function tests, renal function tests and CBC.

Oral Exposure

    6.5.1) PREVENTION OF ABSORPTION/PREHOSPITAL
    A) SUMMARY
    1) Vomiting is rapid and spontaneous in most patients following ingestion of copper salts.
    B) ACTIVATED CHARCOAL
    1) There are no studies demonstrating adsorption of copper to activated charcoal. Most highly charged metal ions are not well adsorbed to activated charcoal. Activated charcoal may obscure endoscopy findings after ingestion of corrosive copper salts as well as creating a risk of corrosive GI perforation with copper. Activated charcoal is NOT recommended in the pre-hospital setting.
    6.5.2) PREVENTION OF ABSORPTION
    A) SUMMARY
    1) Vomiting is rapid and spontaneous in most patients following ingestion of copper salts.
    B) DILUTION
    1) DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting (Caravati, 2004).
    C) NASOGASTRIC SUCTION
    1) Copper salts may be caustic agents, capable of extensive mucosal damage, including perforation of the gastrointestinal tract. Gastric lavage and administration of charcoal may cause further complications. However, some clinicians have successfully used these techniques. These are controversial techniques, and are left to the final judgement of the treating physician.
    2) Some clinicians may choose to insert a small, flexible nasogastric tube through the mouth, if the patient is alert and cooperative, in an attempt to remove the corrosive substance following a recent ingestion.
    a) The decision should be based on the amount of the ingestion, the concentration of the copper sulfate, and the risk and potential benefit to the patient.
    b) In the typical pediatric ingestion involving small volumes of corrosive materials, nasogastric suction is unlikely to be of benefit. In suicidal ingestions involving large quantities of material and an increased likelihood of severe mucosal burns, the risk of causing perforation may outweigh the potential benefit of removing caustic material.
    3) Gastric lavage may be indicated after ingestion of non corrosive forms of copper.
    D) INDICATIONS: Consider gastric lavage with a large-bore orogastric tube (ADULT: 36 to 40 French or 30 English gauge tube {external diameter 12 to 13.3 mm}; CHILD: 24 to 28 French {diameter 7.8 to 9.3 mm}) after a potentially life threatening ingestion if it can be performed soon after ingestion (generally within 60 minutes).
    1) Consider lavage more than 60 minutes after ingestion of sustained-release formulations and substances known to form bezoars or concretions.
    E) PRECAUTIONS:
    1) SEIZURE CONTROL: Is mandatory prior to gastric lavage.
    2) AIRWAY PROTECTION: Place patients in the head down left lateral decubitus position, with suction available. Patients with depressed mental status should be intubated with a cuffed endotracheal tube prior to lavage.
    F) LAVAGE FLUID:
    1) Use small aliquots of liquid. Lavage with 200 to 300 milliliters warm tap water (preferably 38 degrees Celsius) or saline per wash (in older children or adults) and 10 milliliters/kilogram body weight of normal saline in young children(Vale et al, 2004) and repeat until lavage return is clear.
    2) The volume of lavage return should approximate amount of fluid given to avoid fluid-electrolyte imbalance.
    3) CAUTION: Water should be avoided in young children because of the risk of electrolyte imbalance and water intoxication. Warm fluids avoid the risk of hypothermia in very young children and the elderly.
    G) COMPLICATIONS:
    1) Complications of gastric lavage have included: aspiration pneumonia, hypoxia, hypercapnia, mechanical injury to the throat, esophagus, or stomach, fluid and electrolyte imbalance (Vale, 1997). Combative patients may be at greater risk for complications (Caravati et al, 2001).
    2) Gastric lavage can cause significant morbidity; it should NOT be performed routinely in all poisoned patients (Vale, 1997).
    H) CONTRAINDICATIONS:
    1) Loss of airway protective reflexes or decreased level of consciousness if patient is not intubated, following ingestion of corrosive substances, hydrocarbons (high aspiration potential), patients at risk of hemorrhage or gastrointestinal perforation, or trivial or non-toxic ingestion.
    I) ACTIVATED CHARCOAL
    1) There are no studies demonstrating adsorption of copper to activated charcoal. Activated charcoal may obscure endoscopy findings after ingestion of corrosive copper salts and is NOT recommended.
    6.5.3) TREATMENT
    A) HYPOTENSIVE EPISODE
    1) SUMMARY
    a) Infuse 10 to 20 milliliters/kilogram of isotonic fluid and keep the patient supine. If hypotension persists, administer dopamine or norepinephrine. Consider central venous pressure monitoring to guide further fluid therapy.
    2) DOPAMINE
    a) DOSE: Begin at 5 micrograms per kilogram per minute progressing in 5 micrograms per kilogram per minute increments as needed (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). If hypotension persists, dopamine may need to be discontinued and a more potent vasoconstrictor (eg, norepinephrine) should be considered (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    b) CAUTION: If ventricular dysrhythmias occur, decrease rate of administration (Prod Info dopamine hcl, 5% dextrose IV injection, 2004). Extravasation may cause local tissue necrosis, administration through a central venous catheter is preferred (Prod Info dopamine hcl, 5% dextrose IV injection, 2004).
    3) NOREPINEPHRINE
    a) PREPARATION: 4 milligrams (1 amp) added to 1000 milliliters of diluent provides a concentration of 4 micrograms/milliliter of norepinephrine base. Norepinephrine bitartrate should be mixed in dextrose solutions (dextrose 5% in water, dextrose 5% in saline) since dextrose-containing solutions protect against excessive oxidation and subsequent potency loss. Administration in saline alone is not recommended (Prod Info norepinephrine bitartrate injection, 2005).
    b) DOSE
    1) ADULT: Dose range: 0.1 to 0.5 microgram/kilogram/minute (eg, 70 kg adult 7 to 35 mcg/min); titrate to maintain adequate blood pressure (Peberdy et al, 2010).
    2) CHILD: Dose range: 0.1 to 2 micrograms/kilogram/minute; titrate to maintain adequate blood pressure (Kleinman et al, 2010).
    3) CAUTION: Extravasation may cause local tissue ischemia, administration by central venous catheter is advised (Peberdy et al, 2010).
    B) CHELATION THERAPY
    1) SUMMARY: There is little clinical experience in the use of chelators in the setting of acute copper intoxication. Data on efficacy is derived from patients with chronic copper intoxication (Wilson disease, Indian childhood cirrhosis) and animal studies. BAL, penicillamine, DMPS and EDTA have been used. D-penicillamine is considered the drug of choice for Wilson disease, a condition of chronic copper overload.
    2) Chelation therapy is generally recommended in symptomatic patients. If the patient is asymptomatic, confirmation from the laboratory may be received before instituting chelation therapy.
    C) PENICILLAMINE
    1) Penicillamine increases urinary copper excretion in animal models (Owen et al, 1975), complexes copper in vitro (Borchard & Schneider, 1974) and slows or reverses the progression of hepatic disease in patients with chronic copper intoxication (Wilson disease and Indian childhood cirrhosis) (Bhusnurmath et al, 1991; Schilsky et al, 1991).
    a) Penicillamine has been used to treat acute copper intoxication but data regarding efficacy are lacking (Hantson et al, 1996; Jantsch et al, 1985; Holtzman et al, 1966) Rodec et al, 1999).
    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, 2004a; Prod Info DEPEN(R) titratable oral tablets, 2009).
    4) PRECAUTIONS
    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).
    5) ADVERSE EFFECTS
    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).
    6) 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.
    D) DIMERCAPROL
    1) BAL increases urinary copper excretion in patients with Wilson disease (Schilsky et al, 1991) and complexes copper in vitro (Borchard & Schneider, 1974). It has been used in patients with acute copper sulfate intoxication but data regarding efficacy are lacking (Hantson et al, 1996; Jantsch et al, 1985; Walsh et al, 1977; Fairbanks, 1967).
    2) DOSE: BAL (DIMERCAPROL) 3 to 5 milligrams/kilogram/dose deep intramuscularly every 4 hours for 2 days, every 4 to 6 hours for an additional 2 days, then every 4 to 12 hours for up to 7 additional days.
    3) ADVERSE EFFECTS: Adverse reactions such as urticaria may respond to diphenhydramine. Persistent hyperpyrexia is not uncommon.
    E) UNITHIOL
    1) Administration of sodium 2,3-dimercaptopropanesulfonate (DMPS) to mice shortly after copper sulfate intoxication prevented the formation of renal tubular degeneration and renal necrosis as well as hepatic lesions, which are normally seen in mice following copper poisoning (Mitchell et al, 1982).
    2) DMPS is not FDA-approved in the US.
    3) DOSE: 5% solution IM or subcutaneously 5 mg/kg three or four times during the first 24 hours, 2 to 3 times on day two, and 1 to 2 times daily thereafter.
    F) EDETATE CALCIUM DISODIUM
    1) EDTA has been used to treat patients with acute copper sulfate intoxication but data regarding efficacy are lacking (Walsh et al, 1977).
    2) DOSE: 75 milligrams/kilogram/24 hours deep intramuscularly or slow intravenous infusion given in 3 to 6 divided doses up to 5 days; may be repeated for a second course after a minimum of 2 days; each course should not exceed a total of 500 milligrams/kilogram body weight. Complications include renal tubular necrosis, so fluids must be at least maintained and should be intravenous at first.
    G) GENERAL TREATMENT
    1) AMMONIUM THIOMOLYBDATE has been successfully administered to sheep for the prevention and treatment of chronic copper sulfate poisoning (Gooneratne et al, 1981). Use of thiomolybdate for copper toxicity in humans has not been reported, and the material is not readily available.
    H) METHEMOGLOBINEMIA
    1) SUMMARY
    a) Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy.
    2) METHYLENE BLUE
    a) INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules (Prod Info PROVAYBLUE(TM) intravenous injection, 2016) and 10 mg/1 mL (1% solution) vials (Prod Info methylene blue 1% intravenous injection, 2011). REPEAT DOSES: Additional doses may be required, especially for substances with prolonged absorption, slow elimination, or those that form metabolites that produce methemoglobin. NOTE: Large doses of methylene blue may cause methemoglobinemia or hemolysis (Howland, 2006). Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection (Prod Info methylene blue 1% intravenous injection, 2011; Herman et al, 1999). NEONATES: DOSE: 0.3 to 1 mg/kg (Hjelt et al, 1995).
    b) CONTRAINDICATIONS: G-6-PD deficiency (methylene blue may cause hemolysis), known hypersensitivity to methylene blue, methemoglobin reductase deficiency (Shepherd & Keyes, 2004)
    c) FAILURE: Failure of methylene blue therapy suggests: inadequate dose of methylene blue, inadequate decontamination, NADPH dependent methemoglobin reductase deficiency, hemoglobin M disease, sulfhemoglobinemia, or G-6-PD deficiency. Methylene blue is reduced by methemoglobin reductase and nicotinamide adenosine dinucleotide phosphate (NADPH) to leukomethylene blue. This in turn reduces methemoglobin. Red blood cells of patients with G-6-PD deficiency do not produce enough NADPH to convert methylene blue to leukomethylene blue (do Nascimento et al, 2008).
    d) DRUG INTERACTION: Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome (U.S. Food and Drug Administration, 2011; Stanford et al, 2010; Prod Info methylene blue 1% IV injection, 2011).
    3) TOLUIDINE BLUE OR TOLONIUM CHLORIDE (GERMANY)
    a) DOSE: 2 to 4 mg/kg intravenously over 5 minutes. Dose may be repeated in 30 minutes (Nemec, 2011; Lindenmann et al, 2006; Kiese et al, 1972).
    b) SIDE EFFECTS: Hypotension with rapid intravenous administration. Vomiting, diarrhea, excessive sweating, hypotension, dysrhythmias, hemolysis, agranulocytosis and acute renal insufficiency after overdose (Dunipace et al, 1992; Hix & Wilson, 1987; Winek et al, 1969; Teunis et al, 1970; Marquez & Todd, 1959).
    c) CONTRAINDICATIONS: G-6-PD deficiency; may cause hemolysis.
    I) BURN
    1) Some chemicals can produce systemic poisoning by absorption through intact skin. Carefully observe patients with dermal exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.

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.
    6.7.2) TREATMENT
    A) SUPPORT
    1) Copper fumes may cause a metal fume fever syndrome or respiratory signs such as wheezing or rales on auscultation. Be prepared to administer respiratory support to symptomatic patients. Copper may be absorbed by this route and should then be chelated.
    B) Treatment should include recommendations listed in the ORAL EXPOSURE section when appropriate.

Eye Exposure

    6.8.1) DECONTAMINATION
    A) EYE IRRIGATION, ROUTINE: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, an ophthalmologic examination should be performed (Peate, 2007; Naradzay & Barish, 2006).
    6.8.2) TREATMENT
    A) IRRITATION SYMPTOM
    1) Eye contact may result in severe irritation.
    B) Treatment should include recommendations listed in the ORAL EXPOSURE section when appropriate.

Dermal Exposure

    6.9.1) DECONTAMINATION
    A) DECONTAMINATION: Remove contaminated clothing and wash exposed area thoroughly with soap and water for 10 to 15 minutes. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999).
    6.9.2) TREATMENT
    A) IRRITATION SYMPTOM
    1) Skin exposure may result in severe irritation.
    B) SKIN ABSORPTION
    1) Metallic copper embedded in the skin has produced increased serum copper concentrations (Bentur et al, 1988). Monitor serum and urine copper concentrations in patients with significant dermal exposure. Chelation therapy should be considered if copper concentrations are excessive.
    2) CONTACT DERMATITIS - A skin cream containing 10 percent DTPA as a chelator decreased the occurrence of positive patch tests to copper in sensitized individuals (Wohrl et al, 2001).
    C) DISORDER OF HAIR COLOR
    1) GREEN HAIR - Use of shampoos containing penicillamine (250 milligrams in 5 milliliters of water and 5 milliliters of shampoo) (Person, 1985; Mascaro et al, 1995) or EDTA (Goldschmidt, 1979) have been effective in removing green color from hair due to copper exposure.
    D) Treatment should include recommendations listed in the ORAL EXPOSURE section when appropriate.

Enhanced Elimination

    A) HEMODIALYSIS
    1) Hemodialysis was ineffective in a 41-year-old patient who ingested copper sulfate (Agarwal et al, 1975), but may be indicated in patients with renal failure secondary to copper poisoning (Csata et al, 1971).
    B) PERITONEAL DIALYSIS
    1) Continuous peritoneal dialysis with salt-poor albumin over 60 hours resulted in removal of 9.1 milligrams of copper in a child who had ingested approximately 10 to 60 grams of copper sulfate. Concentration of copper in the albumin containing dialysate was 38 micrograms/deciliter, compared with copper concentrations of 3.88 to 4.02 when dialysate without albumin was used. Exchange transfusion was also done during this time and may have contributed to removal of copper (Cole & Lirenman, 1978).

Case Reports

    A) ADULT
    1) ORAL: Chronic ingestion of copper-containing coins in a mentally disturbed patient resulted in severe copper toxicity and death. Copper-containing coins were corroded by prolonged contact with gastric fluids, with subsequent absorption. Deposition of copper was found at autopsy in the liver and kidneys. Death was due to the acute toxic phase of chronic copper poisoning. At autopsy, 275 US coins were found in the stomach (Yelin et al, 1987).
    B) PEDIATRIC
    1) ORAL: Acute ingestion of a refill for a blue ballpoint pen, containing copper phthalocyanines, resulted in nausea and vomiting within a few hours, followed by passage of bright green colored stools within 48 hours in a 2-year-old boy (Forrester, 1975).

Summary

    A) Severe intoxication is associated with serum copper levels greater than 500 mcg/dL. The estimated lethal dose in an untreated adult is 10 to 20 g copper.

Therapeutic Dose

    7.2.1) ADULT
    A) GENERAL
    1) Copper, empirical formula Cu and atomic weight 63.5, is an essential mineral. The average daily diet supplies an adequate 2 to 5 milligrams of copper per day (Baselt, 2000).
    2) The daily requirement has been estimated as 30 mcg/kg for adults (Zenz, 1994).
    7.2.2) PEDIATRIC
    A) GENERAL
    1) The daily requirement has been estimated as 40 mcg/kg for children or 80 mcg/kg for infants (Zenz, 1994).

Minimum Lethal Exposure

    A) The minimum lethal human dose to this agent has not been delineated.
    B) Ingestion of 10 to 20 grams of a soluble copper salt is lethal, and death usually occurs 7 to 10 days after ingestion (Baselt, 2000).
    C) In an untreated adult, an estimated lethal dose is reported to be about 10 to 20 grams of copper (Barceloux, 1999).
    D) CASE REPORTS
    1) Chronic ingestion of copper-containing coins by a mentally disturbed patient resulted in severe copper toxicity and death. At autopsy, 275 US coins were found in the stomach (Yelin et al, 1987).
    2) Hasan et al (1995) reported the death of a mentally handicapped 46-year-old man due to chronic ingestion of British coins. At autopsy, over 700 coins were removed, mostly 1-pence and 2-pence, which were composed of 97 percent copper (Hasan et al, 1995).

Maximum Tolerated Exposure

    A) ROUTE OF EXPOSURE
    1) ORAL
    a) The lowest published toxic dose for humans via the oral route is 120 mcg/kg, with nausea and vomiting reported (RTECS , 2002). The ingestion of as little as one gram of copper may cause toxic serum concentrations (Barceloux, 1999). Ingestion of greater than 25 mg/L copper in beverages or foods has been associated with acute gastroenteritis (Barceloux, 1999).
    b) Tap water copper concentrations of 1 to 2 mg/L have been tolerated by adults with no adverse effects, but are not as well tolerated by children (Nordberg et al, 1985).
    c) Children developed severe liver disorders after ingestion of 10 mg of copper in contaminated milk (Bingham et al, 2001).
    d) In studies of 61 healthy volunteers drinking single 200-mL volumes of copper sulfate, nausea developed at 4 mg/L (33 subjects, concentration as elemental copper) and vomiting developed at 6 mg/L (7 subjects). In this study, 2 mg/L seemed to be generally tolerated (Olivares et al, 2001).
    e) In a study involving 1-week-long exposures to drinking water with varying copper concentrations in a Latin-squares design, no association of gastrointestinal symptoms with cumulative copper intake was noted at concentrations of 0 to 5 mg/L. However, exposure to concentrations of 3 mg/L or more was associated with nausea, abdominal pain and vomiting (Pizarro et al, 1999a; Pizarro et al, 1999b).
    f) The taste threshold for copper in water in the Olivares (2001) study was separately reported to be 2.6 mg/L (Zacarias et al, 2001). Various authors have reported taste thresholds of 0.8 to 5 mg/L copper (Anon, 1998).
    g) CASE REPORT: Two 6-year-old boys (fraternal twins) developed hepatotoxicity following consumption of an energy drink mixed with chocolate milk on a daily basis for the previous 8 months, as well as 2 multivitamins daily. Total amount of copper consumed was 9088 mcg/day, approximately 21 times the recommended daily allowance for their age. Both patients had elevated liver enzyme concentrations; however, a liver biopsy of one of the patients revealed extensive fibrosis with positive staining for copper and a dry copper weight of 1400 mcg/g of liver tissue. Despite chelation therapy with trientine and zinc, the patient developed liver failure within a week of presentation. He received a liver transplant within 72 hours and recovered uneventfully. The second patient's liver biopsy was negative despite a dry copper weight of 3020 mcg/g of liver tissue. He remained stable following chelation therapy with penicillamine. It is suspected that the first patient may have had either underlying liver disease or a possible unidentified defect of copper metabolism, resulting in liver failure despite a dry copper weight of less than half that of his brother (Bartlett & Erickson, 2012).
    2) INHALATION
    a) Inhalation of 60 to 100 mg/kg of copper dust caused gastrointestinal symptoms including vomiting and inflammation (ITI, 1995).
    B) OCCUPATIONAL
    1) Workers exposed to concentrations of one to three mg/m(3) for short periods experienced altered taste response but no nausea. Airborne levels from 0.02 to 0.4 mg/m(3) produced no complaints (Hathaway et al, 1996).
    2) Studies on exposures from industrial copper welding and refining operations in Great Britain indicate that concentrations up to 0.4 mg/m(3) cause no ill effects (ACGIH, 1996).
    a) However, another study reported symptoms similar to metal fume fever in workers exposed to metallic copper dust at an airborne concentration of 0.1 mg/m(3) (ACGIH, 1996).
    C) OTHER
    1) COPPER VESSELS: Preparation of food (particularly acidic foods) in copper vessels with loss of the tinned surface has produced gastroenteritis (Gill & Bhagat, 1999).
    a) Indian childhood cirrhosis has been associated with increased hepatic copper concentrations, partly attributable to the use of copper or brass drinking vessels used to prepare animal milk (Bhave et al, 1987).
    b) Beverages (especially those that are acidic) prepared or stored in brass containers may become contaminated by copper ions and cause poisoning when consumed. Symptoms are nausea and vomiting, which may occur within 10 minutes of consumption.
    2) TAP WATER: Excessive copper in tap water may occur as a result of leaching of copper from pipes; acidity increases the leaching (Spitalny et al, 1984; Prociv, 1997).

Serum Plasma Blood Concentrations

    7.5.2) TOXIC CONCENTRATIONS
    A) TOXIC CONCENTRATION LEVELS
    1) GENERAL
    a) Mean normal serum blood levels of copper are reported as 109 micrograms percent (range 89 to 137 micrograms percent) in men, and 120 micrograms percent (range 87 to 153 micrograms percent) in women (Walsh et al, 1977). Severe intoxication or lethality has been associated with serum copper levels greater than 500 micrograms percent (Holtzman et al, 1966; Agarwal et al, 1975).
    b) Normal copper concentration in blood is about 1 mg/L, although this may vary during pregnancy or with infection (Zenz, 1994). Whole blood copper concentrations near 3 mg/L are associated with gastrointestinal symptoms (Barceloux, 1999).
    c) Chronic poisoning from continuous ingestion of smaller doses of copper may not elicit clinical effects until a threshold storage capacity of hepatocytes for copper is exceeded, at which point lysis of these cells results in acute cupremia with increased serum copper levels. Thus, excessive serum copper levels may not be detected until hepatocytolytic crisis occurs. Because of rapid renal clearance, these later increased levels return to normal within days (Prociv, 1997).
    d) CASE REPORT - A serum copper concentration of 33 mcmol/L was reported in a 41-year-old woman 3 days after injecting herself subcutaneously with 2.5 grams of copper as copper glycinate (Oon et al, 2006).
    e) CASE REPORT - A serum copper concentration of 320 micrograms percent (reference interval 180 to 250) was reported in a 19-year-old man who intentionally ingested a glassful of liquid pesticide containing an unknown amount of copper oxychloride (Gunay et al, 2006).
    f) CASE SERIES - Serum copper concentrations ranged from 190 to 270 micrograms percent (reference interval 180 to 250) in 4 patients following chronic oral exposure to copper oxychloride (Gunay et al, 2006).

Workplace Standards

    A) ACGIH TLV Values for CAS7440-50-8 (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) Copper, fume
    a) TLV:
    1) TLV-TWA: 0.2 mg/m(3)
    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): Irritation; GI; metal fume fever
    d) Molecular Weight: 63.55
    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) Copper, dusts and mists, as Cu
    a) TLV:
    1) TLV-TWA: 1 mg/m(3)
    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): Irritation; GI; metal fume fever
    d) Molecular Weight: 63.55
    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 CAS7440-50-8 (National Institute for Occupational Safety and Health, 2007):
    1) Listed as: Copper (dusts and mists, as Cu)
    2) REL:
    a) TWA: 1 mg/m(3)
    b) STEL:
    c) Ceiling:
    d) Carcinogen Listing: (Not Listed) Not Listed
    e) Skin Designation: Not Listed
    f) Note(s): [*Note: The REL also applies to other copper compounds (as Cu) except Copper fume.]
    3) IDLH:
    a) IDLH: 100 mg Cu/m3 (as Cu)
    b) Note(s): Not Listed

    C) Carcinogenicity Ratings for CAS7440-50-8 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Copper, fume
    2) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Copper, dusts and mists, as Cu
    3) EPA (U.S. Environmental Protection Agency, 2011): D ; Listed as: Copper
    a) D : Not classifiable as to human carcinogenicity.
    4) 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): Not Listed
    5) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Copper (dusts and mists, as Cu)
    6) MAK (DFG, 2002): Not Listed
    7) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    D) OSHA PEL Values for CAS7440-50-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Listed as: Copper Fume (as Cu)
    2) Table Z-1 for Copper Fume (as Cu):
    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: 0.1
    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: Copper Dusts and mists (as Cu)
    4) Table Z-1 for Copper Dusts and mists (as Cu):
    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: 1
    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

Toxicity Information

    7.7.1) TOXICITY VALUES
    A) References: RTECS, 2002 ITI, 1995
    1) LD50- (INTRAPERITONEAL)MOUSE:
    a) 3500 mcg/kg

Pharmacologic Mechanism

    A) Copper is essential for the function of many enzymes such as catalase and peroxidase, and is an important catalyst for heme synthesis and iron absorption (Barceloux, 1999; Goldfrank, 1998).

Toxicologic Mechanism

    A) HEMOLYSIS - Copper produces hemolysis by increasing oxidation of hemoglobin sulfhydryl groups, leading to increased red blood cell permeability (Metz & Sagone, 1972).
    B) FREE OXYGEN RADICALS - Copper inhibits the sulfhydryl group enzymes such as G6PD and glutathione reductase, which protect the cell from free oxygen radicals (Baxter et al, 2000a; Dash, 1989).
    1) Sokol et al (1994) found lipid peroxidation and copper content to be significantly increased in mitochondria from patients with Wilson disease, an idiopathic copper toxicosis, indicating hepatic mitochondrion to be an important target in hepatic copper toxicity, with an involvement of oxidant damage to the liver.
    2) Copper influences gene expression and is a co-factor for oxidative enzymes such as superoxide dismutase, cytochrome C oxidase and lysyl oxidase, as well as for aminolevulonic acid (Baxter et al, 2000a).
    C) ARTERIAL KETONE BODY RATIO - It has been suggested that the maintenance of the arterial ketone body ratio in acute copper sulfate poisoning, in the relatively oxidized redox state of the liver mitochondria (with severe hypovolemic shock), is probably a result of a direct action of the copper ion strongly oxidizing NADPH to NADP+ (Nakatani et al, 1994).

Physical Characteristics

    A) Copper is a lustrous, ductile, malleable, odorless solid with a distinct golden-red or reddish-brown color (ACGIH, 1996; Budavari, 2000; Lewis, 2000; NIOSH , 2002).
    1) In water, the color of copper is often blue or green (OHM/TADS , 2002).
    2) When exposed to moist air, copper gradually develops a coating of green basic carbonate (Budavari, 2000).
    3) Copper salts are usually blue or green in color (ACGIH, 1996).
    B) Workers exposed to copper fume may note a metallic or sweet taste (Hathaway et al, 1991).
    C) Copper has a face-centered cubic structure (Budavari, 2000).

Molecular Weight

    A) 63.546

Other

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

Clinical Effects

    11.1.2) BOVINE/CATTLE
    A) Signs of copper toxicosis (hyperexcitability, hypermetria, hindlimb weakness, head pressing, depression, and opisthotonus) occurred 6 to 24 hours after subcutaneous injection of 120 mg of copper to calves over 150 kg and 60 mg to calves less than 150 kg, as copper disodium edetate. Necropsy showed massive liver necrosis (Bulgin et al, 1986).
    B) CHRONIC COPPER TOXICOSIS results in a sudden onset of hemolytic crisis after gradual copper accumulation in the liver. Trembling, weakness, anorexia, icterus, and hemoglobinuria are frequently seen (Banton et al, 1987).
    11.1.3) CANINE/DOG
    A) Incidence of copper toxicosis is high in Bedlington terriers. As many as 66 percent may have copper-related liver disease (Stockman, 1988).
    B) Dogs may experience a hemolytic crisis (Beasley et al, 1989), but this is not a consistent finding (Noaker et al, 1999).
    C) Acute hepatic failure was reported in a 1.5-year-old Dalmatian dog with high serum copper concentrations (Noaker et al, 1999).
    11.1.4) CAPRINE/GOAT
    A) Goats are 3 to 4 times more tolerant of large amounts of copper than sheep (Beasley et al, 1989).
    11.1.5) EQUINE/HORSE
    A) Horses are relatively resistant to copper poisoning. Experimental toxicosis by subcutaneous injection of 4 mg Cu/kg as copper D-penicillamine in a horse caused hypersensitivity within 5 minutes. Trembling, defecation, and collapse followed. Signs of abdominal pain, sweating, and purple urine were noticed until recovery at 36 hours after the treatment (Auer et al, 1989).
    11.1.9) OVINE/SHEEP
    A) Sheep are commonly affected animals; usually occurs when sheep are fed complete cattle, horse, or poultry diets. Sheep exhibit acute signs, including hemolytic crisis and death, after a long period of excessive copper uptake; morbidity is usually 5% or less but mortality is over 75% (Howard, 1986).
    B) Sheep are highly susceptible to copper poisoning. Copper poisoning was diagnosed in two sheep. The animals had no known copper exposure except the commercial mineral mixture. Before death the animals showed pyrexia, dehydration, icterus, and pasty, golden feces. Serum was hemolyzed, with high nucleated erythrocyte count (13 and 26/100 WBC), neutrophilia and azotemia (150 mg/dL). Urine was cloudy brown, acidic and contained blood and protein. Necropsy indicated icteric connective tissue, and multifocal, irregular, pale areas in the subendocardial myocardium. Livers were smaller, firmer, and showed hepatocellular loss, vacuolization, and swelling in the centrilobular areas. Necrotic hepatocytes and pyknotic nuclei were scattered in liver parenchyma. Kidneys were enlarged and bulged. The poisoning was presumably due to incorrect copper/molybdenum ratio in the mineral supplement (Martin et al, 1988).
    C) Chronic copper poisoning (source unknown) was associated with polioencephalomalacia in a 10-month-old ram lamb. The lamb presented with an acute onset of depression and blindness and poor body condition. Treatment with thiamine and dexamethasone for 3 days improved the lamb's condition. Three weeks later, however, he regressed with the same symptoms and became increasingly ataxic with CNS depression, progressing to stupor and eventually death (Sargison et al, 1994).
    11.1.10) PORCINE/SWINE
    A) Swine and sheep are the species most commonly affected by copper toxicosis (Beasley et al, 1989). Signs of toxicity in swine include anorexia, weight loss, weakness, melena, and death (Beasley et al, 1989).
    B) Swine with chronic copper toxicity due to feed containing excessive copper concentrations (700 ppm) resulted in anorexia, weight loss, melena, weakness, and pallor. Necropsy results showed centrilobular liver necrosis and hypochromic anemia with iron deficiency (Hatch et al, 1979).
    11.1.13) OTHER
    A) OTHER
    1) SIGNS - Excessive salivation, vomiting, abdominal pain, diarrhea (greenish tinged feces).
    2) Copper poisoning was reported in four llamas in a zoologic herd and was attributed to excessive dietary intake of this metal. The symptoms were generally similar to those observed in other animals (recumbency, labored breathing, pale mucous membranes, hypothermia, sinus arrhythmia, leukocytosis and high levels of serum aspartate transaminase, lactate dehydrogenase and gamma-glutanyl transferase). Characteristic liver pathology was observed (Junge & Thornburg, 1989).
    3) FERRETS -
    a) Sibling ferrets diagnosed with copper toxicosis were found to have staining of copper deposits in the liver as well as prominent degeneration, necrosis, and hemorrhage involving central and middle hepatic zones (Fox et al, 1994).
    b) Copper toxicosis in sibling ferrets resulted in hemoglobin casts with renal tubules, and hemoglobin within Bowman's space. Hemoglobinuric nephrosis was particularly prominent in the proximal convoluted tubules (Fox et al, 1994).
    c) No source of copper intoxication was found in these animals and the disorder was suspected to be inherited.

Treatment

    11.2.1) SUMMARY
    A) GENERAL TREATMENT
    1) Begin treatment immediately.
    2) Keep animal warm and do not handle unnecessarily.
    3) Sample vomitus, blood, urine, and feces for analysis.
    4) 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) SUMMARY -
    1) Emesis, lavage, activated charcoal, and cathartic are recommended only in the unlikely event of an acute exposure to a large amount of copper. These administrations are NOT indicated in the treatment of animals with chronic exposure or copper storage diseases such as Bedlington terrier storage syndrome.
    b) EMESIS AND LAVAGE -
    1) If within 2 hours of exposure, induce emesis with 1 to 2 milliliters/kilogram syrup of ipecac per os. Dogs may vomit more readily with 1 tablet (6 milligrams) apomorphine diluted in 3 to 5 milliliters water and instilled into the conjunctival sac or per os. Dogs may also be given apomorphine intravenously at 40 micrograms/kilogram. Do not use an emetic if the animal is hypoxic. In the absence of a gag reflex or if vomiting cannot be induced, place a cuffed endotracheal tube and begin gastric lavage. Pass large bore stomach tube and instill 5 to 10 milliliters/kilogram water or lavage solution, then aspirate. Repeat 10 times (Kirk, 1986).
    c) ACTIVATED CHARCOAL -
    1) Administer activated charcoal. Dose: 2 grams/kilogram per os or via stomach tube. Avoid aspiration by proper restraint, careful technique, and if necessary tracheal intubation.
    d) CATHARTIC -
    1) Administer a dose of a saline cathartic such as magnesium or sodium sulfate 20% (sodium sulfate dose is 1 gram/kilogram). If access to these agents is limited, give 5 to 15 milliliters magnesium hydroxide (Milk of Magnesia) per os for dilution.
    2) LARGE ANIMALS
    a) SUMMARY -
    1) Emesis, lavage, activated charcoal, and cathartic are recommended only in the unlikely event of an acute exposure to a large amount of copper. These administrations are NOT indicated in the treatment of animals with chronic exposure or acute signs of chronic exposure.
    b) EMESIS -
    1) Do not attempt to induce emesis in ruminants (cattle) or equids (horses).
    c) ACTIVATED CHARCOAL -
    1) Adult horses: administer 0.5 to 1 kilogram of activated charcoal in up to 1 gallon warm water via nasogastric tube.
    2) Neonates: administer 250 grams (one-half pound) activated charcoal in up to 2 quarts water.
    3) Adult cattle: administer 2 to 9 grams/ kilogram of activated charcoal in a slurry of 1 gram charcoal/3 to 5 milliliters warm water via stomach tube.
    4) Sheep may be given 0.5 kilogram charcoal in slurry.
    d) CATHARTIC -
    1) Administer an oral cathartic:
    a) Mineral oil (small ruminants and swine, 60 to 200 milliliters; equids and cattle, 0.5 to 1 gallon) or
    b) Magnesium sulfate (ruminants and swine, 1 to 2 grams/kilogram; equine, 0.2 to 0.9 grams/kilogram) or
    c) Milk of Magnesia (small ruminants, up to 0.25 gram/kilogram in 1 to 3 gallons warm water; adult cattle up to 1 gram/kilogram in 1 to 3 gallons warm water or 2 to 4 boluses Mg(OH)2 per os).
    2) Give these solutions via stomach tube and monitor for aspiration.
    11.2.5) TREATMENT
    A) DOG
    1) ACUTE OVERDOSE
    a) MAINTAIN VITAL FUNCTIONS - as necessary.
    b) FLUIDS - If necessary, begin fluid therapy at maintenance doses (66 milliliters solution/kilogram body weight/day intravenously) or, in hypotensive patients, at high doses (up to shock dose 60 milliliters/kilogram/hour). Monitor for urine production and pulmonary edema. Add dextrose and KCl to fluids as needed to prevent hypokalemia and hypoglycemia.
    c) TRANSFUSION - If in hemolytic crisis, transfuse with whole blood or plasma, 25 milliliters/kilogram.
    d) HEPATIC DAMAGE - Treat for acute hepatic failure including cleansing enemas, antibiotics, dietary restrictions, and controlling coagulopathies or gastrointestinal bleeding.
    e) GLUCOCORTICOIDS - Courses of medium-dose glucocorticoids are sometimes beneficial.
    f) ASCORBIC ACID - Ascorbic acid can be given at 500 to 1,000 milligrams/day to enhance urinary excretion of copper.
    g) 2,2,2 TETRAMINE (TRIENTINE) - Experimental studies suggest trientine may be useful as a chelator during an acute episode. Dosage: 10 to 15 milligrams/kilogram orally twice daily (Kirk, 1989). 2,3,2 tetramine tetrahydrochloride 300 to 600 milligrams/day was considered effective in decreasing mean hepatic copper concentrations and enhancing urinary copper excretion (25-fold with the higher dose) on Bedlington terriers with hereditary copper hepatotoxicosis. Reversal of acute hepatic necrosis and hemolytic anemia was observed in one dog (Twedt et al, 1988).
    2) CHRONIC OVERDOSE
    a) PENICILLAMINE - Penicillamine must be given for months to years to reduce the amount of copper stored in the liver. Dosed at 10 to 15 milligrams/kilogram per os twice daily. A common side effect is vomiting (Beasley et al, 1989).
    b) DIETARY RESTRICTION - No commercial diet is substantially low in copper, so homemade diets may be considered for young dogs who have not yet built up large amounts of copper in their livers (Kirk, 1989).
    c) ZINC - Zinc prevents copper reaccumulation in animals who have gone through chelation therapy. Zinc acetate or sulfate is dosed at 5 to 10 milligrams/kilogram per os twice daily. This treatment is currently experimental and may result in side effects such as hemolytic anemia (Kirk, 1989).
    1) Zinc acetate was used to treat dogs with hepatic copper toxicosis, an autosomal recessive disorder in some dogs. Optimal dosage was 50 to 100 mg orally per day. As plasma zinc concentration increased above 200 mcg/dL, copper uptake was suppressed (Brewer et al, 1992).
    B) RUMINANTS/SWINE
    1) MAINTAIN VITAL FUNCTIONS - Secure airway, supply oxygen, and begin supportive fluid therapy if necessary.
    2) FLUIDS - Administer electrolyte and fluid therapy, orally or parenterally as needed. Maintenance dose of intravenous isotonic fluids for calves and debilitated adult cattle: 140 milliliters/kilogram/day. Dose for rehydration: 50 to 100 milliliters/kilogram given over 4 to 6 hours.
    3) WHOLE BLOOD TRANSFUSIONS - In adult horses, 4 to 8 liters blood are normally transfused at one time. This amount of fresh blood may be collected from a single healthy adult donor that has not been bled in the last 30 days. Epinephrine should be available in case of transfusion reaction. Dose: 3 to 5 milliliters 1:1000 dilution intravenously.
    4) PENICILLAMINE - Dosed orally at 11 milligrams/kilogram four times daily for 7 to 10 days.
    5) MOLYBDATE - Ammonium or sodium molybdate is dosed at 50 to 500 milligrams/day orally (Howard, 1986).
    6) THIOSULFATE - Dosed at 0.3 to 1 gram/day orally for up to 3 weeks (Howard, 1986). Dietary supplementation with sodium molybdate (0.5 gram/cow/day) and sodium thiosulfate (5 grams/cow/day) ameliorated signs of chronic copper toxicosis in cattle (Banton et al, 1987).
    7) SHEEP
    a) Intravenous injection of tetrathiomolybdate in copper-loaded sheep reduced the copper concentration in liver and reduced the number and size of electron-dense lysosomes in hepatocytes (Kumaratilake & Howell, 1989a).
    b) Subcutaneous injections of ammonium tetrathiomolybdate (3.4 mg/kg, three doses on alternate days) were effective in substantial reduction of copper content in liver and liver damage in copper poisoned sheep (Humphries et al, 1988).
    c) Ammonium molybdate in a dose of 300 mg orally per day was administered for 4 weeks to ewes exhibiting signs of copper intoxication (Kerr & McGavin, 1991).
    d) Sodium thiosulfate in a dose of 500 mg orally per day was administered for 4 weeks to ewes exhibiting signs of copper intoxication (Kerr & McGavin, 1991).

Range Of Toxicity

    11.3.1) THERAPEUTIC DOSE
    A) SHEEP
    1) The required ratio of copper to molybdenum in sheep is 6 to 1. If copper rises beyond this level, clinical toxicosis is likely (Beasley et al, 1989).
    11.3.2) MINIMAL TOXIC DOSE
    A) GENERAL
    1) Toxic dose ranges from 20 to 150 mg/kg body weight depending upon species, age, feed type, and health status (Beasley et al, 1989). Copper chloride is 2 to 4 times more toxic than copper sulfate (Howard, 1986).
    B) RUMINANT
    1) 30 to 50 ppm copper in the feed may be toxic to ruminants (Beasley et al, 1989). 200 to 800 mg copper sulfate/kilogram may poison cattle. Sheep may be poisoned by single doses of 20 to 100 mg copper sulfate (Howard, 1986).
    2) CASE REPORT - Copper poisoning was reported in a flock of sheep grazing on pastures fertilized with swine manure. Mean copper concentration in forage samples was 13.25 mg/kg and in soil 26.35 mg/kg (compared to 7.25 mg/kg in soil from an adjacent pasture with no manure application). Molybdenum concentrations in soil was similar to non-treated pastures (Kerr & McGavin, 1991).
    3) A mixture containing 213 mg copper sulfate and 80 mg cobalt chloride given to 2- to 6-week-old lambs caused death, characterized by signs of copper poisoning (MacLeod et al, 1990).
    4) Sheep died in an average of 77 days after feeding on pollutants from a copper work. The intake of copper averaged 467 mg/animal for whole period, the copper concentration in liver was 2138 mg/kg dry matter. Although various other metals were present in pollutant mixture, the symptoms were characteristic of copper poisoning (Vrzgula et al, 1989).
    5) Sheep died of copper poisoning when fed a diet consisting of 80 to 90% palm kernel cake. The cake contained 32 ppm (dry matter) of copper; livers of these sheep had 927 to 3898 ppm copper as dry matter (Chooi et al, 1988).
    C) SWINE
    1) Toxicoses appear when copper concentrations in the feed exceed 100 ppm, especially in the presence of low zinc or iron concentrations in the diet (Howard, 1986).
    D) RODENT
    1) Rats can tolerate levels up to 250 ppm in the feed (Beasley et al, 1989).
    E) POULTRY
    1) Turkey poults can tolerate up to 767 ppm copper in feed for 21 days (Beasley et al, 1989).
    11.3.5) TOXIC TISSUE CONCENTRATIONS
    A) DOG
    1) Hepatic tissue concentration in a dog fatality was reported to be 2,356 micrograms/gram wet weight (reference range, 30 to 100 micrograms/gram). Serum copper concentration was reported to be 163.0 micrograms/deciliter (reference range, 20 to 80 micrograms/deciliter) (Noaker et al, 1999).

Continuing Care

    11.4.1) SUMMARY
    11.4.1.2) DECONTAMINATION/TREATMENT
    A) GENERAL TREATMENT
    1) Begin treatment immediately.
    2) Keep animal warm and do not handle unnecessarily.
    3) Sample vomitus, blood, urine, and feces for analysis.
    4) 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) SUMMARY -
    1) Emesis, lavage, activated charcoal, and cathartic are recommended only in the unlikely event of an acute exposure to a large amount of copper. These administrations are NOT indicated in the treatment of animals with chronic exposure or copper storage diseases such as Bedlington terrier storage syndrome.
    b) EMESIS AND LAVAGE -
    1) If within 2 hours of exposure, induce emesis with 1 to 2 milliliters/kilogram syrup of ipecac per os. Dogs may vomit more readily with 1 tablet (6 milligrams) apomorphine diluted in 3 to 5 milliliters water and instilled into the conjunctival sac or per os. Dogs may also be given apomorphine intravenously at 40 micrograms/kilogram. Do not use an emetic if the animal is hypoxic. In the absence of a gag reflex or if vomiting cannot be induced, place a cuffed endotracheal tube and begin gastric lavage. Pass large bore stomach tube and instill 5 to 10 milliliters/kilogram water or lavage solution, then aspirate. Repeat 10 times (Kirk, 1986).
    c) ACTIVATED CHARCOAL -
    1) Administer activated charcoal. Dose: 2 grams/kilogram per os or via stomach tube. Avoid aspiration by proper restraint, careful technique, and if necessary tracheal intubation.
    d) CATHARTIC -
    1) Administer a dose of a saline cathartic such as magnesium or sodium sulfate 20% (sodium sulfate dose is 1 gram/kilogram). If access to these agents is limited, give 5 to 15 milliliters magnesium hydroxide (Milk of Magnesia) per os for dilution.
    2) LARGE ANIMALS
    a) SUMMARY -
    1) Emesis, lavage, activated charcoal, and cathartic are recommended only in the unlikely event of an acute exposure to a large amount of copper. These administrations are NOT indicated in the treatment of animals with chronic exposure or acute signs of chronic exposure.
    b) EMESIS -
    1) Do not attempt to induce emesis in ruminants (cattle) or equids (horses).
    c) ACTIVATED CHARCOAL -
    1) Adult horses: administer 0.5 to 1 kilogram of activated charcoal in up to 1 gallon warm water via nasogastric tube.
    2) Neonates: administer 250 grams (one-half pound) activated charcoal in up to 2 quarts water.
    3) Adult cattle: administer 2 to 9 grams/ kilogram of activated charcoal in a slurry of 1 gram charcoal/3 to 5 milliliters warm water via stomach tube.
    4) Sheep may be given 0.5 kilogram charcoal in slurry.
    d) CATHARTIC -
    1) Administer an oral cathartic:
    a) Mineral oil (small ruminants and swine, 60 to 200 milliliters; equids and cattle, 0.5 to 1 gallon) or
    b) Magnesium sulfate (ruminants and swine, 1 to 2 grams/kilogram; equine, 0.2 to 0.9 grams/kilogram) or
    c) Milk of Magnesia (small ruminants, up to 0.25 gram/kilogram in 1 to 3 gallons warm water; adult cattle up to 1 gram/kilogram in 1 to 3 gallons warm water or 2 to 4 boluses Mg(OH)2 per os).
    2) Give these solutions via stomach tube and monitor for aspiration.
    11.4.3) TREATMENT
    11.4.3.5) SUPPORTIVE CARE
    A) GENERAL
    1) Treatment is symptomatic and supportive.
    11.4.3.6) OTHER
    A) OTHER
    1) LABORATORY--ANTEMORTEM -
    a) DOG
    1) SGPT may increase late in the disease and indicates hepatocellular injury. There usually is no increase in serum copper levels (Beasley et al, 1989).
    b) RUMINANTS AND SHEEP -
    1) Copper concentrations in the blood of normal healthy animals usually fall between 0.7 and 2 ppm (Howard, 1986).
    2) LABORATORY--POSTMORTEM -
    a) SWINE
    1) Pale liver with centrilobular necrosis, gastric ulcers, pale muscles, and watery blood (Beasley et al, 1989).
    b) DOG
    1) Liver of abnormal size, and microscopic lesions including prominent cytoplasmic granules in hepatocytes and cirrhosis (Beasley et al, 1989).
    c) RUMINANTS AND SHEEP -
    1) Classic postmortem findings include hemoglobinuria, gun-metal colored kidneys, pale or yellow liver, and liver copper concentrations of greater than 150 ppm (wet-weight basis)(Howard, 1986).

Kinetics

    11.5.1) ABSORPTION
    A) SPECIFIC TOXIN
    1) Absorption varies greatly depending on the formulation of the diet and acidity of the intestine (Beasley et al, 1989).
    2) Livers of sheep had 22 to 40 ppm copper when fed a ration with 95 ppm copper and 2.5 ppm molybdenum (Stahr et al, 1989).
    3) Plasma copper level in a horse increased from 0.4 g/mL to 7.7 g/mL at 8 hours after acute copper poisoning. It returned to baseline after 30 hours (Auer et al, 1989).
    11.5.2) DISTRIBUTION
    A) SPECIFIC TOXIN
    1) After absorption, copper is 90% protein bound (Beasley et al, 1989).
    2) Sheep dosed with 0.2% solution of copper sulfate at the rate of 15 mL/kg body weight (30 mg copper sulfate/kg) daily contained 1061 ppm copper in kidney cortex and 2500 ppm copper in liver during the hemolytic stage (Gooneratne et al, 1989a). High levels of copper were localized in the nuclear and cytosolic fractions of kidney cortex (compared to mitochondrial and microsomal fractions). The distribution of copper in the cytosolic fraction was altered after treatment with thiomolybdate; the absolute copper level increased but percent of total copper in tissue decreased (Gooneratne et al, 1989b).
    3) The increase in the copper concentration after copper dosing was primarily in lysosomes and cytosolic fraction in sheep liver (Kumaratilake & Howell, 1989b).
    11.5.3) METABOLISM
    A) SPECIFIC TOXIN
    1) In the liver, copper is incorporated into the mitochondria, microsomes, nuclei, and cytosol of hepatocytes (Beasley et al, 1989).
    11.5.4) ELIMINATION
    A) SPECIFIC TOXIN
    1) Copper is eliminated into the bile, feces, and urine. The majority is excreted in the feces.

Pharmacology Toxicology

    A) SPECIFIC TOXIN
    1) Chronic copper poisoning of sheep caused a linear increase in hepatocytic lysosomes, except the lysosomes decreased during hemolysis. It was suggested that the necrosis of hepatocytes packed with electron-dense lysosomes resulted due to high accumulation of copper in these organelles (Kumaratilake & Howell, 1989c).
    2) SHEEP - The acute signs follow a chronic overingestion of copper and buildup in the liver. The acute episode is usually brought on by some stress factor which correlates with massive copper release from the damaged liver. Hemolysis results, leading to anemia, icterus, hemoglobinemia, renal failure, and death within 24 to 48 hours after onset of signs (Beasley et al, 1989).

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) ACGIH: Documentation of the Threshold Limit Values and Biological Exposure Indices (Supplement), 6th ed, Am Conference of Govt Ind Hyg, Inc, Cincinnati, OH, 1996a.
    14) ACGIH: Documentation of the Threshold Limit Values and Biological Exposure Indices, (Supplement) 6th ed, Am Conference of Govt Ind Hyg, Inc, Cincinnati, OH, 1996.
    15) ACGIH: Documentation of the Threshold Limit Values and Biological Exposure Indices, 6th ed, Am Conference of Govt Ind Hyg, Inc, Cincinnati, OH, 1991.
    16) AIHA: 2006 Emergency Response Planning Guidelines and Workplace Environmental Exposure Level Guides Handbook, American Industrial Hygiene Association, Fairfax, VA, 2006.
    17) Adams CD, Fusco W, & Kanzelmeyer T: Ozone, hydrogen peroxide/ozone and UV/ozone treatment of chromium- and copper-complex dyes: decolorization and metal release. Ozone-Sci Eng 1995; 17:149-162.
    18) Agarwal BN, Bray SH, & Bercz P: Ineffectiveness of hemodialysis in copper sulphate poisoning. Nephron 1975; 15:74-77.
    19) Agarwal SK, Tiwari SC, & Dash SC: Spectrum of poisoning requiring haemodialysis in tertiary care hospital in India. Internat J Artif Organs 1993; 16:20-22.
    20) Akintonwa A, Mabadeje AFB, & Odutola TA: Fatal poisoning by copper sulfate ingested from "spiritual water. Vet Human Toxicol 1989; 31:453-454.
    21) Alloway BJ: Heavy Metals in Soils, Blackie & Son Ltd, Glasgow, Scotland, 1990.
    22) Alva AK, Graham JH, & Tucker DPH: Role of calcium in amelioration of copper phytotoxicity for citrus. Soil Sci 1993; 155:211-218.
    23) American Conference of Governmental Industrial Hygienists : ACGIH 2010 Threshold Limit Values (TLVs(R)) for Chemical Substances and Physical Agents and Biological Exposure Indices (BEIs(R)), American Conference of Governmental Industrial Hygienists, Cincinnati, OH, 2010.
    24) Anon: Copper (Environmental Health Criteria #200), World Health Organization, Geneva, Switzerland, 1998.
    25) Anon: Cutis laxa and other congenital defects with penicillamine, ADR Highlights (Division of drug experience), Rockville, MD, 1981, pp 1-4-81-21.
    26) Armstrong CW, Moore LW, & Hackler RL: An outbreak of metal fume fever. J Occup Med 1983; 25:886-888.
    27) Ashford RD: Ashford's Dictionary of Industrial Chemicals, Wavelength Publications, London, United Kingdom, 1994.
    28) Atkinson D, Beasley M, & Dryburgh P: Accidental subcutaneous copper salt injection: toxic effects and management. NZ Med J 2004; 117:800-805.
    29) Auer DE, Ng JC, & Seawrite AA: A suspected case of acute copper toxicity in a horse. Aust Vet J 1989; 66:191-192.
    30) Baghramian SB: ZH Arm 1975; 28:56-62.
    31) Banton MI, Nicholson SS, & Jowett PLH: Copper toxicosis in cattle fed chicken litter. JAVMA 1987; 191:827-828.
    32) Barceloux DG: Copper. Clin Toxicol 1999; 37:217-230.
    33) Barranco VP: Eczematous dermatitis caused by internal exposure to copper. Arch Dermatol 1972; 106:386-387.
    34) Bartlett MG & Erickson NI: Copper overload in 6-year-old twins. J Pediatr Gastroenterol Nutr 2012; 55(6):e145-e147.
    35) Baselt RC: Disposition of Toxic Drugs and Chemicals in Man, 5th ed, Chemical Toxicology Institute, Foster City, CA, 2000.
    36) Baxter PJ, Adams PH, & Aw TC: Hunter's Diseases of Occupations, 9th ed, Oxford University Press Inc, New York, NY, 2000.
    37) Baxter PJ, Adams PH, & Aw TC: Hunter's Diseases of Occupations, 9th ed, Oxford University Press Inc, New York, NY, 2000a.
    38) Beasley VR, Dorman DC, & Fikes JD: A Systems Affected Approach to Veterinary Toxicology, University of Illinois, Urbana, IL, 1989.
    39) Beck RB, Rosenbaum KN, & Byers PH: Ultrastructural findings in fetal penicillamine syndrome, 14th March of Dimes Ann Birth Defects Conf, San Diego, CA, 1981.
    40) Bennetts HW & Chapman FE: Aust Vet J 1937; 13:138-149.
    41) Bentur Y, Koren G, & McGuigan M: An unusual skin exposure to copper: clinical and pharmacokinetic evalution. Clin Toxicol 1988; 26:371-380.
    42) Bhave SA, Pandit AN, & Tanner MS: Comparison of feeding history of children with Indian childhood cirrhosis and paired controls. J Pediatr Gastroenterol Nutrition 1987; 6:562-567.
    43) Bhunya SP & Jena GB: Clastogenic effects of copper sulphate in chick in vivo test system. Mutat Res 1996; 367:57-63.
    44) Bhusnurmath SR, Walia BNS, & Singh S: Sequential histopathologic alterations in Indian childhood cirrhosis treated with d-Penicillamine. Human Pathol 1991; 22:653-658.
    45) Bingham E, Chorssen B, & Powell CH: Patty's Toxicology, Vol. 2, 5th ed, John Wiley & Sons, New York, NY, 2001a.
    46) Bingham E, Cohrssen B, & Powell CH: Patty's Toxicology, Vol. 2, 5th ed, John Wiley & Sons, New York, NY, 2001.
    47) Bloomfield J: Arch Int Med 1971; 128:555-560.
    48) Bockendahl H: Arch Dermatol Fors 1974; 260:161-167.
    49) Borak J, Cohen H, & Hethmon TA: Copper exposure and metal fume fever: lack of evidence for a causal relationship. AIHAJ 2000; 61:832-836.
    50) Borchard U & Schneider KU: Intoxication, detoxication and copper-storage of central nervous tissue a different external Cu(II)-concentrations. Arch Toxicol 1974; 33:17-30.
    51) Boyd W & Williams P: Comparison of the sensitivity of three nematode species to copper and their utility in aquatic and soil toxicity tests. Environmental Toxicology and Chemistry 2003; 22/11:2768-2774.
    52) Bremner I: Manifestations of copper excess. Am J Clin Nutr 1998; 67(Suppl):1069S-1073S.
    53) Brewer GJ, Dick RD, & Schall W: Use of zinc acetate to treat copper toxicosis in dogs. JAVMA 1992; 201:564-568.
    54) Brinser RL & Cross PC: Nature 1972; 238:398-399.
    55) Brodskii I: Arch Gewerbepathol Gewerbehyg 1933; 5:91.
    56) Buchwald A: Serum copper elevation from estrogen effect, masquerading as fungicide toxicity. J Med Toxicol 2008; 4(1):30-32.
    57) Budavari S: The Merck Index, 12th ed, Merck & Co, Inc, Whitehouse Station, NJ, 1996.
    58) Budavari S: The Merck Index, 12th ed. on CD-ROM. Version 12:3a. Chapman & Hall/CRCnetBASE. Whitehouse Station, NJ. 2000.
    59) Bulgin MS, Maas J, & Anderson BC: Death associated with parenteral administration of copper disodium edetate in calves. JAVMA 1986; 188:406-409.
    60) Burgess JL, Kirk M, Borron SW, et al: Emergency department hazardous materials protocol for contaminated patients. Ann Emerg Med 1999; 34(2):205-212.
    61) Burnett JW: Copper. Cutis 1989; 43:322.
    62) Caravati EM, Knight HH, & Linscott MS: Esophageal laceration and charcoal mediastinum complicating gastric lavage. J Emerg Med 2001; 20:273-276.
    63) Caravati EM: Alkali. In: Dart RC, ed. Medical Toxicology, Lippincott Williams & Wilkins, Philadelphia, PA, 2004.
    64) Caravati EM: D-Penicillamine. In: Dart RC, ed. Medical Toxicology, Lippincott Williams & Wilkins, Philadelphia, PA, 2004a.
    65) Chang CC: Fertil Steril 1970; 21:274-278.
    66) Chen RL, Wei L, & Huang HM: Mortality from lung cancer among copper miners. Br J Ind Med 1993; 50:505-509.
    67) Chin RKH: Pregnancy and Wilson's disease (Letter). Am J Obstet Gynecol 1991; 165:488.
    68) Chooi KF, Hutagalung RI, & Mohamed WW: Copper toxicity in sheep fed oil palm byproducts. Aust Vet J 1988; 65:156-157.
    69) Chugh KS, Sharma BK, & Singhal PC: Acute renal failure following copper sulphate intoxication. Postgrad Med J 1977; 53:18.
    70) Chugh KS, Sharma BK, & Singhal PC: Methemoglobinemia in acute copper sulphate poisoning. Ann Intern med 1975; 82:226.
    71) Chugh KS, Singhal PC, & Sharma BK: Acute renal failure due to intravascular hemolysis in North Indian patients. Am J Med Sci 1977a; 274:139.
    72) Chuttani HK, Gupta PS, & Gulati S: Acute copper sulfate poisoning. Am J Med 1965; 39:849-854.
    73) Clayton GD & Clayton FE: Patty's Industrial Hygiene and Toxicology, Toxicology, 4th ed, 2A, John Wiley & Sons, New York, NY, 1994.
    74) Clayton GD & Clayton FE: Patty's Industrial Hygiene and Toxicology, Vol 2A, Toxicology, 3rd ed, John Wiley & Sons, New York, NY, 1981.
    75) Cole DEC & Lirenman DS: Role of albumin-enriched peritoneal dialysate in acute copper poisoning. J Pediatr 1978; 92:955-956.
    76) Cordier S: Environ Res 1983; 31:311-322.
    77) Creason JP: Trace Subs Environ Health 1976; 10:53-62.
    78) Csata S, Gallyas F, & Frang D: Nephrotoxic anuria. Internat Urol Nephrol 1971; 3:181-201.
    79) DFG: List of MAK and BAT Values 2002, Report No. 38, Deutsche Forschungsgemeinschaft, Commission for the Investigation of Health Hazards of Chemical Compounds in the Work Area, Wiley-VCH, Weinheim, Federal Republic of Germany, 2002.
    80) Dash SC: Copper sulphate poisoning and acute renal failure. Internat J Artif Organs 1989; 12:610.
    81) Dayan MR, Cottrell DG, & Mitchell KW: Reversible retinal toxicity associated with retained intravitreal copper foreign body in the absence of intraocular inflammation. Acta Ophthalmol Scand 1999; 77:597-598.
    82) Denny P, Bailey R, & Tukahirwa E: Heavy metal contamination of Lake George (Uganda) and its wetlands. Hydrobiologia 1995; 297:229-239.
    83) Dowdy RP: Copper metabolism. Am J Clin Nutr 1969; 22:887-892.
    84) Downey D: Porphyria induced by palladium-copper dental prostheses: a clinical report. J Prosthet Dent 1992; 67:5-6.
    85) DuPont P, Irion O, & Beguin F: Pregnancy and Wilson's disease (Reply). Am J Obstet Gynecol 1991; 165:489.
    86) Duffy RE, Brown SE, & Caldwell KL: An epidemic of corneal destruction caused by plasma gas sterilization. Arch Ophthalmol 2000; 118:1167-1176.
    87) Dunipace AJ, Beaven R, Noblitt T, et al: Mutagenic potential of toluidine blue evaluated in the Ames test. Mutat Res 1992; 279(4):255-259.
    88) Dushenkov V, Kumar P, & Motto H: Rhizofiltration: the use of plants to remove heavy metals from aqueous streams. Environ Sci Technol 1995; 29:1239-1245.
    89) EPA: Search results for Toxic Substances Control Act (TSCA) Inventory Chemicals. US Environmental Protection Agency, Substance Registry System, U.S. EPA's Office of Pollution Prevention and Toxics. Washington, DC. 2005. Available from URL: http://www.epa.gov/srs/.
    90) ERG: Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of a Dangerous Goods/Hazardous Materials Incident, U.S. Department of Transportation, Research and Special Programs Administration, Washington, DC, 2004.
    91) Eastwood JB, Phillips ME, & Minty P: Heparin inactivation, acidosis and copper poisoning due to presumed acid contamination of water in a hemodialysis unit. Clin Nephrol 1983; 20:197-201.
    92) Eife R, Weiss M, & Barros V V: Chronic poisoning by copper in tap water: I. Copper intoxications with predominantly gastointestinal symptoms. Eur J Med Res 1999a; 4:219-223.
    93) Eife R, Weiss M, & Muller-Hocker M: Chronic poisoning by copper in tap water: II. Copper intoxications with predominantly systemic symptoms. Eur J Med Res 1999b; 4:224-228.
    94) Enterline PE & Marsh GM: Am J Epidemiol 1982; 116:895-911.
    95) Everson GJ & Wang TI: Fed Proc 1967; 26:633.
    96) Fairbanks VF: Copper sulfate-induced hemolytic anemia. Arch Int Med 1967; 120:428-432.
    97) Feehally J, Wheeler DC, Mackay EH, et al: Recurrent acute renal failure with interstitial nephritis due to D-penicillamine. Renal Failure 1987; 10:55-57.
    98) Ferm VH & Hanlon DP: Biol Reprod 1974; 11:97-101.
    99) Ford ES: Serum copper concentration and coronary heart disease among US adults. Am J Epidemiol 2000; 151:1182-1188.
    100) Forrester RM: Poison pen? (letter). Lancet 1975; 1:468.
    101) Fox JG, Zeman DH, & Mortimer JD: Copper toxicosis in sibling ferrets. J Am Vet Med Assoc 1994; 205:1154-1156.
    102) Freeman HM: Standard Handbook of Hazardous Waste Treatment and Disposal, 2nd ed, McGraw-Hill Book Company, New York, NY, 1998.
    103) Friberg L: Handbook on the Toxicology of Metals, Vols I & II, Elsevier, Amsterdam, 1986.
    104) Giavini E: Bull Environ Contam Toxicol 1980; 25:702-705.
    105) Gill JS & Bhagat CI: Acute copper poisoning from drinking lime cordial prepared and left overnight in an old urn (letter). Med J Aust 1999; 170:510.
    106) Goldfrank LR: Goldfrank's Toxicological Emergencies, 6th ed, McGraw-Hill, New York, NY, 1998.
    107) Goldschmidt H: Green hair. Arch Dermatol 1979; 115:1288.
    108) Gooneratne SR, Gawthorne JM, & Howell JM: Distribution of Cu, Zn, and Fe in the soluble fraction of the kidney in normal, copper-poisoned and thiomolybdate-treated sheep. J Inorg Biochem 1989b; 35:37-53.
    109) Gooneratne SR, Howell JM, & Gawthorne JM: Subcellular distribution of copper in the kidneys of normal, copper-poisoned, and thiomolybdate-treated sheep. J Inorg Biochem 1989a; 35:23-36.
    110) Gorell JM, Johnson CC, & Rybicki BA: Occupational exposure to manganese, copper, lead, iron, mercury and zinc and the risk of Parkinson's disease. Neurotoxicol 1999; 20:239-247.
    111) Graham J, Russo C, Huntington S, et al: Organic Copper Algaecide Toxicity: Case Report and Statewide Poison Center Exposures Review (abstracts). Clin Toxicol (Phila) 2015; 53(7):772.
    112) Grant WM & Schuman JS: Toxicology of the Eye, 4th ed, Charles C Thomas, Springfield, IL, 1993.
    113) Gulliver JM: A fatal copper sulfate poisoning. J Anal Toxicol 1991; 15:341-342.
    114) Gunay N, Yildirim C, Karcioglu O, et al: A series of patients in the emergency department diagnosed with copper poisoning: recognition equals treatment. Tohoku J Exp Med 2006; 209(3):243-248.
    115) HSDB : Hazardous Substances Data Bank. National Library of Medicine. Bethesda, MD (Internet Version). Edition expires 1/31/2002; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    116) HSDB : Hazardous Substances Data Bank. National Library of Medicine. Bethesda, MD (Internet Version). Edition expires 2004; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    117) HSDB : Hazardous Substances Data Bank. National Library of Medicine. Bethesda, MD (Internet Version). Edition expires 4/30/2001; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    118) HSDB: Hazardous Substances Data Bank. National Library of Medicine. Bethesda, MD (Internet Version). Edition expires 2002; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    119) Han BC, Jeng WL, & Tsai YN: Depuration of copper and zinc by green oysters and blue mussels of Taiwan. Environ Pollut 1993; 82:93-97.
    120) Handy RD: The effect of acute exposure to dietary Cd and Cu on organ toxicant concentrations in rainbow trout, Oncorhynchus mykiss. Aquat Toxicol 1993; 27:1-14.
    121) Hantson P, Lievens M, & Mahieu P: Accidental ingestion of a zinc and copper sulfate preparation. Clin Toxicol 1996; 34:724-730.
    122) Harbison RD: Hamilton & Hardy's Industrial Toxicology, 5th ed, Mosby-Year Books, St. Louis, MO, 1998.
    123) Harris ZL & Gitlin JD: Genetic and molecular basis for copper toxicity. Am J Clin Nutr 1996; 63:S836-S841.
    124) Hasan N, Emery D, & Baithun SI: Chronic copper intoxication due to ingestion of coins: a report of an unusual case. Human Exp Toxicol 1995; 14:500-502.
    125) Hatch RC, Blue JL, & Mahaffey EA: Chronic copper toxicosis in growing swine. J Am Vet Med Assoc 1979; 147:616-619.
    126) Hathaway GJ, Proctor NH, & Hughes JP: Chemical Hazards of the Workplace, 3rd ed, Van Nostrand Reinhold Company, New York, NY, 1991.
    127) Hathaway GJ, Proctor NH, & Hughes JP: Chemical Hazards of the Workplace, 4th ed, Van Nostrand Reinhold Company, New York, NY, 1996.
    128) Hemminki K: Internat Arch Occup Environ Health 1980; 45:123-126.
    129) Hemminki K: in: Clarkson TW et al (Eds), Reproductive and Developmental Toxicity of Metals, Plenum Press, New York, NY, 1983, pp 369-380.
    130) Herman MI, Chyka PA, & Butlse AY: Methylene blue by intraosseous infusion for methemoglobinemia. Ann Emerg Med 1999; 33:111-113.
    131) Hix WR & Wilson WR: Toluidine blue staining of the esophagus: a useful adjunct in the panendoscopic evaluation of patients with squamous cell carcinoma of the head and neck. Arch Otolaryngol Head Neck Surg 1987; 113(8):864-865.
    132) Hjelt K, Lund JT, Scherling B, et al: Methaemoglobinaemia among neonates in a neonatal intensive care unit. Acta Paediatr 1995; 84(4):365-370.
    133) Hogg DS, Mclaren RG, & Swift RS: Desorption of copper from some New-Zealand soils. Soil Sci Soc Am J 1993; 57:361-366.
    134) Hole LM, Moore MN, & Bellamy D: Age-related cellular reactions to copper in the marine mussel Mytilus edulis. Mar Ecol-Progr Ser 1993; 94:175-179.
    135) Holtzman NA, Elliott DA, & Heller RH: Copper intoxication. Report of a case with observations on ceruloplasmin. N Engl J Med 1966; 275:347-352.
    136) Horslen SP, Tanner MS, & Lyon TDB: Copper associated childhood cirrhosis. Gut 1994; 35:1497-1500.
    137) Hoveyda N, Yates B, Bond CR, et al: A cluster of cases of abdominal pain possibly associated with high copper levels in a private water supply. J Environ Health 2003; 66:29-32.
    138) Howard JL: Current Veterinary Therapy: Food Animal Practice 2, Saunders, Philadelphia, PA, 1986.
    139) Howland MA: Antidotes in Depth. In: Goldfrank LR, Flomenbaum N, Hoffman RS, et al, eds. Goldfrank's Toxicologic Emergencies. 8th ed., 8th ed. McGraw-Hill, New York, NY, 2006, pp 826-828.
    140) Humphries WR, Morrice PC, & Bremner I: A convenient method for the treatment of chronic copper poisoning in sheep using subcutaneous ammonium tetrathiomolybdate. Vet Rec 1988; 123:51-53.
    141) Hyvarinen H & Nygren T: Accumulation of copper in the liver of moose in Finland. J Wildlife Manage 1993; 57:469-474.
    142) IARC Working Group on the Evaluation of Carcinogenic Risks to Humans : IARC Monographs on the Evaluation of Carcinogenic Risks to Humans: 1,3-Butadiene, Ethylene Oxide and Vinyl Halides (Vinyl Fluoride, Vinyl Chloride and Vinyl Bromide), 97, International Agency for Research on Cancer, Lyon, France, 2008.
    143) IARC Working Group on the Evaluation of Carcinogenic Risks to Humans : IARC Monographs on the Evaluation of Carcinogenic Risks to Humans: Formaldehyde, 2-Butoxyethanol and 1-tert-Butoxypropan-2-ol, 88, International Agency for Research on Cancer, Lyon, France, 2006.
    144) IARC Working Group on the Evaluation of Carcinogenic Risks to Humans : IARC Monographs on the Evaluation of Carcinogenic Risks to Humans: Household Use of Solid Fuels and High-temperature Frying, 95, International Agency for Research on Cancer, Lyon, France, 2010a.
    145) IARC Working Group on the Evaluation of Carcinogenic Risks to Humans : IARC Monographs on the Evaluation of Carcinogenic Risks to Humans: Smokeless Tobacco and Some Tobacco-specific N-Nitrosamines, 89, International Agency for Research on Cancer, Lyon, France, 2007.
    146) IARC Working Group on the Evaluation of Carcinogenic Risks to Humans : IARC Monographs on the Evaluation of Carcinogenic Risks to Humans: Some Non-heterocyclic Polycyclic Aromatic Hydrocarbons and Some Related Exposures, 92, International Agency for Research on Cancer, Lyon, France, 2010.
    147) IARC: List of all agents, mixtures and exposures evaluated to date - IARC Monographs: Overall Evaluations of Carcinogenicity to Humans, Volumes 1-88, 1972-PRESENT. World Health Organization, International Agency for Research on Cancer. Lyon, FranceAvailable from URL: http://monographs.iarc.fr/monoeval/crthall.html. As accessed Oct 07, 2004.
    148) ICAO: Technical Instructions for the Safe Transport of Dangerous Goods by Air, 2003-2004. International Civil Aviation Organization, Montreal, Quebec, Canada, 2002.
    149) ILO : Encyclopedia of Occupational Health and Safety, 4th ed. Vol 1-4. (CD ROM Version). International Labour Organization. Geneva, Switzerland. 1998.
    150) ILO: Encyclopaedia of Occupational Health & Safety, 4th ed. Vol 1-4.JM Stellman (Ed), International Labour Organization, Geneva, Switzerland, 1998.
    151) ITI: Toxic and Hazardous Industrial Chemicals Safety Manual, The International Technical Information Institute, Tokyo, Japan, 1995.
    152) International Agency for Research on Cancer (IARC): IARC monographs on the evaluation of carcinogenic risks to humans: list of classifications, volumes 1-116. International Agency for Research on Cancer (IARC). Lyon, France. 2016. Available from URL: http://monographs.iarc.fr/ENG/Classification/latest_classif.php. As accessed 2016-08-24.
    153) International Agency for Research on Cancer: IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. World Health Organization. Geneva, Switzerland. 2015. Available from URL: http://monographs.iarc.fr/ENG/Classification/. As accessed 2015-08-06.
    154) Jacobson PJ, Farris JL, & Cherry DS: Juvenile freshwater mussel (Bivalvia, Unionidae) responses to acute toxicity testing with copper -- short communication. Environ Toxicol Chem 1993; 12:879-883.
    155) James LF: Am J Vet Res 1966; 27:132-135.
    156) Jankowski MA, Uriuhare JY, & Rucker RB: Effect of maternal diabetes and dietary copper on fetal development in rats. Reprod Toxicol 1993; 7:589-598.
    157) Jantsch W, Kulig K, & Rumack BH: Massive copper sulfate ingestion resulting in hepatotoxicity. Clin Toxicol 1985; 22:585-588.
    158) Junge RE & Thornburg L: Copper poisoning in four llamas. JAVMA 1989; 195:987-989.
    159) Kay A: European league against rheumatism study of adverse reactions to D-penicillamine. Br J Rheumatol 1986; 25:193-198.
    160) Kerr LA & McGavin HD: Chronic copper poisoning in sheep grazing pastures fertilized with swine manure. JAVMA 1991; 198:99-101.
    161) Kiese M , Lorcher W , Weger N , et al: Comparative studies on the effects of toluidine blue and methylene blue on the reduction of ferrihaemoglobin in man and dog. Eur J Clin Pharmacol 1972; 4(2):115-118.
    162) Kim S & Chomchai S: Elevated serum copper levels and methemoglobinemia from residential exposure to copper naphthenate (abstract). J Toxicol-Clin Toxicol 1999; 37:622.
    163) Kirk RW: Current Veterinary Therapy IX, Saunders, Philadelphia, PA, 1986.
    164) Kirk RW: Current Veterinary Therapy X, Saunders, Philadelphia, PA, 1989.
    165) Kirk-Othmer: Encyclopedia of Chemical Technology, Vol 4, 4th ed, John Wiley & Sons, New York, NY, 1992.
    166) Kirk-Othmer: Encyclopedia of Chemical Technology, Vol 4, 4th ed, John Wiley and Sons, New York, NY, 1992a.
    167) Kisters K, Spieker C, & Fafera I: Copper, zinc and plasma and intracellular magnesium concentrations in pregnancy and pre-eclampsia. Trace Elem Med 1993; 10:158-162.
    168) Klein WJ, Metz EN, & Price AR: Acute intoxication. A hazard of hemodialysis. Arch Intern Med 1972; 129:578.
    169) Kleinman ME, Chameides L, Schexnayder SM, et al: 2010 American Heart Association guidelines for cardiopulmonary resuscitation and emergency cardiovascular care. Part 14: pediatric advanced life support. Circulation 2010; 122(18 Suppl.3):S876-S908.
    170) Knobeloch L, Schubert C, & Hayes J: Gastrointestinal upsets and new copper plumbing - is there a connection?. WMJ 1998; 97:49-53.
    171) Kuhnert BR, Kuhnert PM, & Lazebnik N: The relationship between placental cadmium, zinc, and copper. J Am Coll Nutr 1993; 12:31-35.
    172) Kumaratilake JS & Howell JM: Intracellular distribution of copper in the liver of copper loaded sheep -- a subcellular fractionation study. J Comp Pathol 1989a; 101:161-176.
    173) Kumaratilake JS & Howell JM: Intravenously administered tetrathiomolybdate and the removal of copper from the liver of copper-loaded sheep. J Comp Pathol 1989b; 101:177-199.
    174) Kumaratilake JS & Howell JM: Lysosomes in the pathogenesis of liver injury in chronic copper poisoned sheep: an ultrastructural and morphometric study. J Comp Pathol 1989c; 100:381-390.
    175) Kurisaki E, Kuroda Y, & Sato M: Copper-binding protein in acute copper poisoning. Forens Sci Internat 1988; 38:3-11.
    176) Lai CH, Lo SL, & Lin CF: Evaluating an iron-coated sand for removing copper from water. Water Sci Tech 1994; 30:175-182.
    177) Lehman RM & Mills AL: Field evidence for copper mobilization by dissolved organic matter. Water Res 1994; 28:2487-2497.
    178) Lewis JW, Kay AN, & Hanna NS: Responses of Electric Fish (Family Mormyridae) to chemical changes in water quality. 3. heavy metals. Environ Technol 1994; 15:969-978.
    179) Lewis RJ: Hawley's Condensed Chemical Dictionary, 12th ed, Van Nostrand Reinhold Company, New York, NY, 1993.
    180) Lewis RJ: Hawley's Condensed Chemical Dictionary, 13th ed, John Wiley & Sons, Inc, New York, NY, 1997a.
    181) Lewis RJ: Hawley's Condensed Chemical Dictionary, 13th ed, Van Nostrand Reinhold Co, New York, NY, 1997.
    182) Lewis RJ: Sax's Dangerous Properties of Industrial Materials, 10th ed, Van Nostrand Reinhold Company, New York, NY, 2000.
    183) Likhaechev IuP, Batsura IuD, & Direev VI: The role of several occupational factors in the development of pulmonary alveolar proteinosis (an experimental study). Arkhiv Patologii 1975; 37:63-69.
    184) Lin HC & Dunson WA: The effect of salinity on the acute toxicity of cadmium to the tropical, estuarine, hermaphroditic fish, Rivulus marmoratus: a comparison of Cd, Cu, and Zn tolerance with Fundulus heteroclitus. Arch Environ Contam Toxicol 1993; 25:41-7.
    185) Linares A, Zarranz JJ, & Rodrigues-Alarcon J: Reversible cutis laxa due to maternal d-penicillamine treatment. Lancet 1979; 2:43.
    186) Lindenmann J, Matzi V, Kaufmann P, et al: Hyperbaric oxygenation in the treatment of life-threatening isobutyl nitrite-induced methemoglobinemia--a case report. Inhal Toxicol 2006; 18(13):1047-1049.
    187) Linder MC & Hazeghazam M: Copper biochemistry and molecular biology. Am J Clin Nutr 1996; 63:S797-S811.
    188) Logue JN: J Occup Med 1982; 24:398-408.
    189) Loven A, Romem Y, & Pelly IZ: Copper metabolism - a factor in gestational diabetes. Clin Chim ACTA 1992; 213:51-59.
    190) Low KS, Lee CK, & Leo AC: Removal of metals from electroplating wastes using banana pith. Bioresource Technol 1995; 51:227-231.
    191) MMWR: Methemoglobinemia in an infant -- Wisconsin, 1992. MMWR: MMWR 1993; 42:217-219.
    192) MacLeod NSM, Bonn JM, & Struthers J: Deaths in lamb following overdose with a copper/cobalt mixture. Vet Rec 1990; 126:648-649.
    193) Madaric A, Ginter E, & Kadrabova J: Serum copper, zinc and copper/zinc ratio in males: influence of aging. Physiol Res 1994; 43:107-111.
    194) Marquez A & Todd M: Acute hemolytic anemia and agranulocytosis following intravenous administration of toluidine blue. Am Pract 1959; 10:1548-1550.
    195) Martin BJ, Dysko RC, & Chrisp CE: Copper poisoning in sheep. Lab Anim Sci 1988; 38:734-736.
    196) Marzin DR & Phi HV: Mutat Res 1985; 155:49-51.
    197) Mascaro JM, Ferrando J, & Fontarnau R: Green hair (continuing medical education). Cutis 1995; 56:37-40.
    198) Matter BJ, Pederson JG, & Psimenos G: Lethal copper intoxication in hemodialysis. Trans Am Soc Artif Int Org 1969; 15:309.
    199) Meghji S, Haque MF, & Harris M: Oral submucous fibrosis and copper (letter). Lancet 1997; 350:220.
    200) Metz EN & Sagone AL: The effect of copper on the erythrocyte hexose monophosphate shunt pathway. J Lab Clin Med 1972; 80:405-413.
    201) Mishra U, Kashyap AK, & Pandey J: Effects of copper on photopigments and photosystem-II activity of cyanophage N-1 resistant mutant. Environ Technol 1993; 14:373-378.
    202) Morris P, O'Neill, & Tanner S: Synergistic liver toxicity of copper and retrosine in the rat. J Hepatol 1994; 21:735-742.
    203) Muller T, Feichtinger H, & Berger H: Endemic Tyrolean infantile cirrhosis -- an ecogenetic disorder. Lancet 1996; 347:877-880.
    204) Muller T, Muller W, & Feichtinger H: Idiopathic copper toxicosis. Am J Clin Nutr 1998; 67(Suppl):1082S-1086S.
    205) Muller-Hocker J, Summer KH, & Schramel P: Different pathomorphologic patterns in exogenic infantile copper intoxication of the liver. Pathol Res Pract 1998; 194:377-384.
    206) NFPA: Fire Protection Guide to Hazardous Materials, 12th ed, National Fire Protection Association, Quincy, MA, 1997.
    207) NFPA: Fire Protection Guide to Hazardous Materials, 13th ed., National Fire Protection Association, Quincy, MA, 2002.
    208) NIOSH : Pocket Guide to Chemical Hazards (Internet Version). National Institute for Occupational Safety and Health. Cincinnati, OH (Internet Version). Edition expires 1/31/2002; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    209) NIOSH : Pocket Guide to Chemical Hazards (Internet Version). National Institute for Occupational Safety and Health. Cincinnati, OH (Internet Version). Edition expires 4/30/2001; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    210) NRC: Acute Exposure Guideline Levels for Selected Airborne Chemicals - Volume 1, Subcommittee on Acute Exposure Guideline Levels, Committee on Toxicology, Board on Environmental Studies and Toxicology, Commission of Life Sciences, National Research Council. National Academy Press, Washington, DC, 2001.
    211) NRC: Acute Exposure Guideline Levels for Selected Airborne Chemicals - Volume 2, Subcommittee on Acute Exposure Guideline Levels, Committee on Toxicology, Board on Environmental Studies and Toxicology, Commission of Life Sciences, National Research Council. National Academy Press, Washington, DC, 2002.
    212) NRC: Acute Exposure Guideline Levels for Selected Airborne Chemicals - Volume 3, Subcommittee on Acute Exposure Guideline Levels, Committee on Toxicology, Board on Environmental Studies and Toxicology, Commission of Life Sciences, National Research Council. National Academy Press, Washington, DC, 2003.
    213) NRC: Acute Exposure Guideline Levels for Selected Airborne Chemicals - Volume 4, Subcommittee on Acute Exposure Guideline Levels, Committee on Toxicology, Board on Environmental Studies and Toxicology, Commission of Life Sciences, National Research Council. National Academy Press, Washington, DC, 2004.
    214) NRC: Drinking Water and Health. National Academy of Sciences, 1, National Academy Press, Washington, DC, 1988.
    215) Nakatani T, Spolter L, & Kobayashi K: Redox state in liver mitochondria in acute copper sulfate poisoning. Life Sciences 1994; 54:967-974.
    216) Naradzay J & Barish RA: Approach to ophthalmologic emergencies. Med Clin North Am 2006; 90(2):305-328.
    217) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for 1,2,3-Trimethylbenzene (Proposed). United States Environmental Protection Agency. Washington, DC. 2006k. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d68a&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    218) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for 1,2,4-Trimethylbenzene (Proposed). United States Environmental Protection Agency. Washington, DC. 2006m. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d68a&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    219) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for 1,2-Butylene Oxide (Proposed). United States Environmental Protection Agency. Washington, DC. 2008d. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648083cdbb&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    220) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for 1,2-Dibromoethane (Proposed). United States Environmental Protection Agency. Washington, DC. 2007g. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064802796db&disposition=attachment&contentType=pdf. As accessed 2010-08-18.
    221) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for 1,3,5-Trimethylbenzene (Proposed). United States Environmental Protection Agency. Washington, DC. 2006l. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d68a&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    222) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for 2-Ethylhexyl Chloroformate (Proposed). United States Environmental Protection Agency. Washington, DC. 2007b. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648037904e&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    223) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Acrylonitrile (Proposed). United States Environmental Protection Agency. Washington, DC. 2007c. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648028e6a3&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    224) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Adamsite (Proposed). United States Environmental Protection Agency. Washington, DC. 2007h. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020fd29&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    225) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Agent BZ (3-quinuclidinyl benzilate) (Proposed). United States Environmental Protection Agency. Washington, DC. 2007f. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064803ad507&disposition=attachment&contentType=pdf. As accessed 2010-08-18.
    226) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Allyl Chloride (Proposed). United States Environmental Protection Agency. Washington, DC. 2008. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648039d9ee&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    227) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Aluminum Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005b. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    228) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Arsenic Trioxide (Proposed). United States Environmental Protection Agency. Washington, DC. 2007m. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480220305&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    229) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Automotive Gasoline Unleaded (Proposed). United States Environmental Protection Agency. Washington, DC. 2009a. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7cc17&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    230) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Biphenyl (Proposed). United States Environmental Protection Agency. Washington, DC. 2005j. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064801ea1b7&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    231) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Bis-Chloromethyl Ether (BCME) (Proposed). United States Environmental Protection Agency. Washington, DC. 2006n. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648022db11&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    232) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Boron Tribromide (Proposed). United States Environmental Protection Agency. Washington, DC. 2008a. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064803ae1d3&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    233) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Bromine Chloride (Proposed). United States Environmental Protection Agency. Washington, DC. 2007d. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648039732a&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    234) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Bromoacetone (Proposed). United States Environmental Protection Agency. Washington, DC. 2008e. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064809187bf&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    235) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Calcium Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005d. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    236) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Carbonyl Fluoride (Proposed). United States Environmental Protection Agency. Washington, DC. 2008b. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064803ae328&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    237) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Carbonyl Sulfide (Proposed). United States Environmental Protection Agency. Washington, DC. 2007e. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648037ff26&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    238) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Chlorobenzene (Proposed). United States Environmental Protection Agency. Washington, DC. 2008c. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064803a52bb&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    239) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Cyanogen (Proposed). United States Environmental Protection Agency. Washington, DC. 2008f. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064809187fe&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    240) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Dimethyl Phosphite (Proposed). United States Environmental Protection Agency. Washington, DC. 2009. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7cbf3&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    241) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Diphenylchloroarsine (Proposed). United States Environmental Protection Agency. Washington, DC. 2007l. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020fd29&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    242) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Ethyl Isocyanate (Proposed). United States Environmental Protection Agency. Washington, DC. 2008h. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648091884e&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    243) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Ethyl Phosphorodichloridate (Proposed). United States Environmental Protection Agency. Washington, DC. 2008i. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480920347&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    244) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Ethylbenzene (Proposed). United States Environmental Protection Agency. Washington, DC. 2008g. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064809203e7&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    245) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Ethyldichloroarsine (Proposed). United States Environmental Protection Agency. Washington, DC. 2007j. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020fd29&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    246) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Germane (Proposed). United States Environmental Protection Agency. Washington, DC. 2008j. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480963906&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    247) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Hexafluoropropylene (Proposed). United States Environmental Protection Agency. Washington, DC. 2006. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064801ea1f5&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    248) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Ketene (Proposed). United States Environmental Protection Agency. Washington, DC. 2007. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020ee7c&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    249) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Magnesium Aluminum Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005h. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    250) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Magnesium Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005g. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    251) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Malathion (Proposed). United States Environmental Protection Agency. Washington, DC. 2009k. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064809639df&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    252) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Mercury Vapor (Proposed). United States Environmental Protection Agency. Washington, DC. 2009b. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a8a087&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    253) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Methyl Isothiocyanate (Proposed). United States Environmental Protection Agency. Washington, DC. 2008k. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480963a03&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    254) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Methyl Parathion (Proposed). United States Environmental Protection Agency. Washington, DC. 2008l. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480963a57&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    255) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Methyl tertiary-butyl ether (Proposed). United States Environmental Protection Agency. Washington, DC. 2007a. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064802a4985&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    256) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Methylchlorosilane (Proposed). United States Environmental Protection Agency. Washington, DC. 2005. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5f4&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    257) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Methyldichloroarsine (Proposed). United States Environmental Protection Agency. Washington, DC. 2007i. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020fd29&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    258) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Methyldichlorosilane (Proposed). United States Environmental Protection Agency. Washington, DC. 2005a. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c646&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    259) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Nitrogen Mustard (HN1 CAS Reg. No. 538-07-8) (Proposed). United States Environmental Protection Agency. Washington, DC. 2006a. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d6cb&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    260) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Nitrogen Mustard (HN2 CAS Reg. No. 51-75-2) (Proposed). United States Environmental Protection Agency. Washington, DC. 2006b. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d6cb&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    261) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Nitrogen Mustard (HN3 CAS Reg. No. 555-77-1) (Proposed). United States Environmental Protection Agency. Washington, DC. 2006c. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d6cb&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    262) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Nitrogen Tetroxide (Proposed). United States Environmental Protection Agency. Washington, DC. 2008n. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648091855b&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    263) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Nitrogen Trifluoride (Proposed). United States Environmental Protection Agency. Washington, DC. 2009l. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480963e0c&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    264) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Parathion (Proposed). United States Environmental Protection Agency. Washington, DC. 2008o. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480963e32&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    265) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Perchloryl Fluoride (Proposed). United States Environmental Protection Agency. Washington, DC. 2009c. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7e268&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    266) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Perfluoroisobutylene (Proposed). United States Environmental Protection Agency. Washington, DC. 2009d. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7e26a&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    267) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Phenyl Isocyanate (Proposed). United States Environmental Protection Agency. Washington, DC. 2008p. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648096dd58&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    268) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Phenyl Mercaptan (Proposed). United States Environmental Protection Agency. Washington, DC. 2006d. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020cc0c&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    269) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Phenyldichloroarsine (Proposed). United States Environmental Protection Agency. Washington, DC. 2007k. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020fd29&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    270) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Phorate (Proposed). United States Environmental Protection Agency. Washington, DC. 2008q. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648096dcc8&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    271) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Phosgene (Draft-Revised). United States Environmental Protection Agency. Washington, DC. 2009e. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a8a08a&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    272) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Phosgene Oxime (Proposed). United States Environmental Protection Agency. Washington, DC. 2009f. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7e26d&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    273) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Potassium Cyanide (Proposed). United States Environmental Protection Agency. Washington, DC. 2009g. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7cbb9&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    274) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Potassium Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005c. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    275) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Propargyl Alcohol (Proposed). United States Environmental Protection Agency. Washington, DC. 2006e. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020ec91&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    276) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Selenium Hexafluoride (Proposed). United States Environmental Protection Agency. Washington, DC. 2006f. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020ec55&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    277) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Silane (Proposed). United States Environmental Protection Agency. Washington, DC. 2006g. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d523&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    278) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Sodium Cyanide (Proposed). United States Environmental Protection Agency. Washington, DC. 2009h. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7cbb9&disposition=attachment&contentType=pdf. As accessed 2010-08-15.
    279) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Sodium Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005i. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    280) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Strontium Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005f. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    281) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Sulfuryl Chloride (Proposed). United States Environmental Protection Agency. Washington, DC. 2006h. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020ec7a&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    282) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Tear Gas (Proposed). United States Environmental Protection Agency. Washington, DC. 2008s. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648096e551&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    283) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Tellurium Hexafluoride (Proposed). United States Environmental Protection Agency. Washington, DC. 2009i. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7e2a1&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    284) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Tert-Octyl Mercaptan (Proposed). United States Environmental Protection Agency. Washington, DC. 2008r. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648096e5c7&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    285) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Tetramethoxysilane (Proposed). United States Environmental Protection Agency. Washington, DC. 2006j. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d632&disposition=attachment&contentType=pdf. As accessed 2010-08-17.
    286) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Trimethoxysilane (Proposed). United States Environmental Protection Agency. Washington, DC. 2006i. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d632&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    287) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Trimethyl Phosphite (Proposed). United States Environmental Protection Agency. Washington, DC. 2009j. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=0900006480a7d608&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    288) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Trimethylacetyl Chloride (Proposed). United States Environmental Protection Agency. Washington, DC. 2008t. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648096e5cc&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    289) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for Zinc Phosphide (Proposed). United States Environmental Protection Agency. Washington, DC. 2005e. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020c5ed&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    290) National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances: Acute Exposure Guideline Levels (AEGLs) for n-Butyl Isocyanate (Proposed). United States Environmental Protection Agency. Washington, DC. 2008m. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=09000064808f9591&disposition=attachment&contentType=pdf. As accessed 2010-08-12.
    291) National Heart,Lung,and Blood Institute: Expert panel report 3: guidelines for the diagnosis and management of asthma. National Heart,Lung,and Blood Institute. Bethesda, MD. 2007. Available from URL: http://www.nhlbi.nih.gov/guidelines/asthma/asthgdln.pdf.
    292) National Institute for Occupational Safety and Health: NIOSH Pocket Guide to Chemical Hazards, U.S. Department of Health and Human Services, Centers for Disease Control and Prevention, Cincinnati, OH, 2007.
    293) National Research Council : Acute exposure guideline levels for selected airborne chemicals, 5, National Academies Press, Washington, DC, 2007.
    294) National Research Council: Acute exposure guideline levels for selected airborne chemicals, 6, National Academies Press, Washington, DC, 2008.
    295) National Research Council: Acute exposure guideline levels for selected airborne chemicals, 7, National Academies Press, Washington, DC, 2009.
    296) National Research Council: Acute exposure guideline levels for selected airborne chemicals, 8, National Academies Press, Washington, DC, 2010.
    297) Nelson LS: Copper. In: Nelson LS, Hoffman RS, Lewin NA, et al, eds. Goldfrank's Toxicologic Emergencies, 9th ed. McGraw Hill Medical, New York, NY, 2011, pp 1256-1265.
    298) Nemec K: Antidotes in acute poisoning. Eur J Hosp Pharm Sci Pract 2011; 17(4):53-55.
    299) Noaker LJ, Washabau RJ, & Detrisac CJ: Copper associated acute hepatic failure in a dog. J Am Vet Med Assc 1999; 214:1502-1506.
    300) Nonnotte L, Boitel F, & Truchot JP: Waterborne copper causes gill damage and hemolymph hypoxia in the shore crab Carcinus maenas. Canad J Zool 1993; 71:1569-1576.
    301) Nordberg GF, Goyer RA, & Clarkson TW: Impact of effects of acid precipitation on toxicity of metals. Environ Health Perspect 1985; 63:169-180.
    302) O'Dell BL: J Nutr 1961; 73:151-157.
    303) O'Donohue J, Reid M, & Varghese A: A case of adult chronic copper self-intoxication resulting in cirrhosis. Eur J Med Res 1999; 4:252.
    304) O'Neill NC & Tanner MS: Uptake of copper from brass vessels by bovine milk and its relevance to Indian childhood cirrhosis. J Pediatr Gastroenterol Nutr 1989; 9:167-172.
    305) OHM/TADS : Oil and Hazardous Materials/Technical Assistance Data System. US Environmental Protection Agency. Washington, DC (Internet Version). Edition expires 1/31/2002; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    306) OHM/TADS : Oil and Hazardous Materials/Technical Assistance Data System. US Environmental Protection Agency. Washington, DC (Internet Version). Edition expires 4/30/2001; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    307) OHM/TADS: Oil and Hazardous Materials/Technical Assistance Data System. US Environmental Protection Agency. Washington, DC (Internet Version). Edition expires 2001; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    308) OSHA: Personal Protective Equipment for General Industry. 59 FR 16334-16364, 59, Department of Labor, Occupational Safety and Health Administration, Washington, DC, 2000, pp 16334-16364.
    309) Olivares M, Araya M, & Pizarro F: Nausea threshold in apparently healthy individuals who drink fluids containing graded concentrations of copper. Regul Toxicol Pharmacol 2001; 33:271-275.
    310) Oon S, Yap CH, & Ihle BU: Acute copper toxicity following copper glycinate injection. Intern Med J 2006; 36(11):741-743.
    311) Overvad K, Wang DY, & Olsen J: Copper in human mammary carcinogenesis -- a case-cohort study. Am J Epidemiol 1993; 137:409-414.
    312) Peate WF: Work-related eye injuries and illnesses. Am Fam Physician 2007; 75(7):1017-1022.
    313) Peberdy MA , Callaway CW , Neumar RW , et al: 2010 American Heart Association guidelines for cardiopulmonary resuscitation and emergency cardiovascular care science. Part 9: post–cardiac arrest care. Circulation 2010; 122(18 Suppl 3):S768-S786.
    314) Pellegrini M, Laugier A, & Sergent M: Interactions between the toxicity of the heavy metals cadmium, copper, zinc in combinations and the detoxifying role of calcium in the brown alga Cystoseira barbata. J Appl Phycol 1993; 5:351-361.
    315) Person JR: Green hair: treatment with a penicillamine shampoo (Letter). Arch Dermatol 1985; 121:717-718.
    316) Phillips MJ, Ackerley CA, & Superina RA: Excess zinc associated with severe progressive cholestasis in Cree and Ojibwa-Cree children. Lancet 1996; 347:866-868.
    317) Pizarro F, Olivares M, & Gidi V: The gastrointestinal tract and acute effects of copper in drinking water and beverages. Rev Environ Health 1999a; 14:231-238.
    318) Pizarro F, Olivares M, & Uauy R: Acute gastrointestinal effects of graded levels of copper in drinking water. Environ Health Perspect 1999b; 107:117-121.
    319) Pohanish RP & Greene SA: Rapid Guide to Chemical Incompatibilities, Van Reinhold Company, New York, NY, 1997.
    320) Porta AA & Ronco AE: Cu(II) acute toxicity to the rotifer Brachionus calyciflorus, as affected by fulvic acids of freshwater origin. Environ Pollut 1993; 82:263-267.
    321) Price LA, Walker NI, & Clague AE: Chronic copper toxicosis presenting as liver failure in an Australian child. Pathology 1996; 28:316-320.
    322) Prociv P: Excess copper in a local water supply (letter). Med J Aust 1997; 166:224.
    323) Proctor NH & Hughes JP: Chemical Hazards of the Workplace, JB Lippincott Co, Philadelphia, PA, 1978.
    324) Product Information: CUPRIMINE(R) oral capsules, penicillamine oral capsules. Merck & Co,Inc, Whitehouse Station, NJ, 2004.
    325) Product Information: DEPEN(R) titratable oral tablets, penicillamine titratable oral tablets. Meda Pharmaceuticals Inc, Somerset, NJ, 2009.
    326) Product Information: PROVAYBLUE(TM) intravenous injection, methylene blue intravenous injection. American Regent (per FDA), Shirley, NY, 2016.
    327) Product Information: dopamine hcl, 5% dextrose IV injection, dopamine hcl, 5% dextrose IV injection. Hospira,Inc, Lake Forest, IL, 2004.
    328) Product Information: methylene blue 1% IV injection, methylene blue 1% IV injection. American Regent, Inc (per manufacturer), Shirley, NY, 2011.
    329) Product Information: methylene blue 1% intravenous injection, methylene blue 1% intravenous injection. Akorn, Inc. (per manufacturer), Lake Forest, IL, 2011.
    330) Product Information: norepinephrine bitartrate injection, norepinephrine bitartrate injection. Sicor Pharmaceuticals,Inc, Irvine, CA, 2005.
    331) Pujol RM, Randazzo L, & Miralles J: Perimenstrual dermatitis secondary to a copper-containing intrauterine contraceptive device. Contact Dermatitis 1998; 38:288.
    332) RTECS : Registry of Toxic Effects of Chemical Substances. National Institute for Occupational Safety and Health. Cincinnati, OH (Internet Version). Edition expires 1/31/2002; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    333) RTECS : Registry of Toxic Effects of Chemical Substances. National Institute for Occupational Safety and Health. Cincinnati, OH (Internet Version). Edition expires 4/30/2001; provided by Truven Health Analytics Inc., Greenwood Village, CO.
    334) Reunanen A, Knekt P, & Marniemi J: Serum calcium, magnesium, copper and zinc and risk of cardiovascular death. Eur J Clin Nutrition 1996; 50:431-437.
    335) Roblero L, Guadarrama A, & Lopez T: Effect of copper ion on the motility, viability, acrosome reaction and fertilizing capacity of human spermatozoa in vitro. Reprod Fertil Dev 1996; 8:871-874.
    336) Rosa FW: Teratogen update: penicillamine. Teratology 1986; 33:127-131.
    337) Ross AI: Lancet 1955; 2:87.
    338) Ruffing R: Copper: normal metabolism, poisoning and a review of Palm Island mystery disease (Unpublished). Unpublished, 1988.
    339) Sargison ND, Scott PR, & Penny CD: Polioencephalomalacia associated with chronic copper poisoning in a Suffolk ram lamb. Veterinary Record 1994; 135:556-557.
    340) Schagen van Leeuwen JH & Christiaens GC: Recurrent abortion and the diagnosis of Wilson disease. Obstet Gynecol 1991; 78:547-549.
    341) Schardein JL: Chemically Induced Birth Defects, 3rd ed, Marcel Dekker, Inc, New York, NY, 2000.
    342) Scheinberg IH & Sternlieb I: Is non-Indian childhood cirrhosis caused by excess dietary copper?. Lancet 1994; 344:1002-1004.
    343) Schilsky ML, Scheinberg IH, & Sternlieb I: Prognosis of Wilsonian chronic active hepatitis. Gastroenterology 1991; 100:762-767.
    344) Schubauerberigan MK, Dierkes JR, & Monson PD: pH-dependent toxicity of Cd, Cu, Ni, Pb and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbriculus variegatus. Environ Toxicol Chem 1993; 12:1261-1266.
    345) Schwartz E & Schmidt E: Refractory shock secondary to copper sulfate ingestion. Ann Emerg Med 1986; 15:952-954.
    346) Shepherd G & Keyes DC: Methylene blue. In: Dart,RC, ed. Medical Toxicology, 3rd ed. 3rd ed, Philadelphia, PA, 2004, pp -.
    347) Sittig M: Handbook of Toxic and Hazardous Chemicals and Carcinogens, 3rd ed, Noyes Publications, Park Ridge, NJ, 1991.
    348) Smith CA, Khoury JM, & Shields SM: Unexpected corneal endothelial cell decompensation after intraocular surgery with instruments sterilized by plasma gas. Ophthalmology 2000; 107:1561-1566.
    349) Solomon L, Abrams G, & Dinner M: Neonatal abnormalities associated with d-penicillamine treatment during pregnancy. N Engl J Med 1977; 296:54.
    350) Sorokin VA, Valeev VA, & Gladchenko GO: Interaction of bivalent copper, nickel, manganese ions with native DNA and its monomers. J Inorg Biochem 1996; 63:79-98.
    351) Spitalny KC, Brondum J, & Vogt RL: Drinking water-induced copper intoxication in a Vermont family. Pediatrics 1984; 74:1103-1106.
    352) Stahr HM, Wass WM, & Witte ST: Copper levels in sheep surviving an acute toxic exposure. Vet Human Toxicol 1989; 31:588.
    353) Stanford SC , Stanford BJ , & Gillman PK : Risk of severe serotonin toxicity following co-administration of methylene blue and serotonin reuptake inhibitors: an update on a case report of post-operative delirium. J Psychopharmacol 2010; 24(10):1433-1438.
    354) Stein RS, Jenkins D, & Korns ME: Death after use of cupric sulfate as emetic (Letter). JAMA 1976; 235:801.
    355) Stockman MJR: Copper toxicosis in the Bedlington terrier. Vet Rec 1988; 123:355.
    356) Tanner MS, Bhave SA, & Kantarjian AH: Early introduction of copper-contaminated animal milk feeds as a possible cause of Indian childhood cirrhosis. Lancet 1983; 2:992-995.
    357) Tanner MS: Role of copper in Indian childhood cirrhosis. Am J Clin Nutr 1998; 67(Suppl):1074S-1081S.
    358) Taylor LN, Wood CM, & McDonald DG: An evaluation of sodium loss and gill metal binding properties in rainbow trout and yellow perch to explain species differences in copper tolerance. Environ Toxicol Chem 2003; 22/9:2159-2166.
    359) Teunis BS, Leftwich EI, & Pierce LE: Acute methemoglobinemia and hemolytic anemia due to toluidine blue. Arch Surg 1970; 101:527-531.
    360) Todd JR & Thompson RH: Methemoglobinemia in chronic copper poisoning of sheep. Nature 1961; 191:89.
    361) Tosti A, Mattioli D, & Miscial C: Green hair caused by copper present in cosmetic plant extracts. Dermatol 1991; 182:1204-1205.
    362) Toyokuni S & Sagripanti JL: Increased 8-hydroxydeoxyguanosine in kidney and liver of rats continuously exposed to copper. Toxicol Appl Pharmacol 1994; 126:91-97.
    363) Tubbing DMJ, Santhagens LR, & Admiraal W: Biological and chemical aspects of differences in sensitivity of natural populations of aquatic bacterial communities exposed to copper. Environ Toxic Water Qual 1993; 8:191-205.
    364) Tumer Z & Horn N: Menkes disease -- recent advances and new insights into copper metabolism. Ann Med 1996; 28:121-129.
    365) Twedt DC, Hunsaker HA, & Allen KGD: Use of 2,3,2-tetramine as a hepatic copper chelating agent for treatment of copper hepatotoxicosis in Bedlington terriers. JAVMA 1988; 192:52-56.
    366) U.S. Department of Energy, Office of Emergency Management: Protective Action Criteria (PAC) with AEGLs, ERPGs, & TEELs: Rev. 26 for chemicals of concern. U.S. Department of Energy, Office of Emergency Management. Washington, DC. 2010. Available from URL: http://www.hss.doe.gov/HealthSafety/WSHP/Chem_Safety/teel.html. As accessed 2011-06-27.
    367) U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project : 11th Report on Carcinogens. U.S. Department of Health and Human Services, Public Health Service, National Toxicology Program. Washington, DC. 2005. Available from URL: http://ntp.niehs.nih.gov/INDEXA5E1.HTM?objectid=32BA9724-F1F6-975E-7FCE50709CB4C932. As accessed 2011-06-27.
    368) U.S. Environmental Protection Agency: Discarded commercial chemical products, off-specification species, container residues, and spill residues thereof. Environmental Protection Agency's (EPA) Resource Conservation and Recovery Act (RCRA); List of hazardous substances and reportable quantities 2010b; 40CFR(261.33, e-f):77-.
    369) U.S. Environmental Protection Agency: Integrated Risk Information System (IRIS). U.S. Environmental Protection Agency. Washington, DC. 2011. Available from URL: http://cfpub.epa.gov/ncea/iris/index.cfm?fuseaction=iris.showSubstanceList&list_type=date. As accessed 2011-06-21.
    370) U.S. Environmental Protection Agency: List of Radionuclides. U.S. Environmental Protection Agency. Washington, DC. 2010a. Available from URL: http://www.gpo.gov/fdsys/pkg/CFR-2010-title40-vol27/pdf/CFR-2010-title40-vol27-sec302-4.pdf. As accessed 2011-06-17.
    371) U.S. Environmental Protection Agency: List of hazardous substances and reportable quantities. U.S. Environmental Protection Agency. Washington, DC. 2010. Available from URL: http://www.gpo.gov/fdsys/pkg/CFR-2010-title40-vol27/pdf/CFR-2010-title40-vol27-sec302-4.pdf. As accessed 2011-06-17.
    372) U.S. Environmental Protection Agency: The list of extremely hazardous substances and their threshold planning quantities (CAS Number Order). U.S. Environmental Protection Agency. Washington, DC. 2010c. Available from URL: http://www.gpo.gov/fdsys/pkg/CFR-2010-title40-vol27/pdf/CFR-2010-title40-vol27-part355.pdf. As accessed 2011-06-17.
    373) U.S. Food and Drug Administration: FDA Drug Safety Communication: Serious CNS reactions possible when methylene blue is given to patients taking certain psychiatric medications. U.S. Food and Drug Administration. Silver Spring, MD. 2011. Available from URL: http://www.fda.gov/Drugs/DrugSafety/ucm263190.htm. As accessed 2011-07-26.
    374) U.S. Occupational Safety and Health Administration: Part 1910 - Occupational safety and health standards (continued) Occupational Safety, and Health Administration's (OSHA) list of highly hazardous chemicals, toxics and reactives. Subpart Z - toxic and hazardous substances. CFR 2010 2010; Vol6(SEC1910):7-.
    375) U.S. Occupational Safety, and Health Administration (OSHA): Process safety management of highly hazardous chemicals. 29 CFR 2010 2010; 29(1910.119):348-.
    376) United States Environmental Protection Agency Office of Pollution Prevention and Toxics: Acute Exposure Guideline Levels (AEGLs) for Vinyl Acetate (Proposed). United States Environmental Protection Agency. Washington, DC. 2006. Available from URL: http://www.regulations.gov/search/Regs/contentStreamer?objectId=090000648020d6af&disposition=attachment&contentType=pdf. As accessed 2010-08-16.
    377) Urben PG: Brethrick's Handbook of Reactive Chemical Hazards, Vol. 1, 6th ed, Butterworth-Heinemann Ltd, Oxford, UK, 1999.
    378) Vale JA, Kulig K, American Academy of Clinical Toxicology, et al: Position paper: Gastric lavage. J Toxicol Clin Toxicol 2004; 42:933-943.
    379) Vale JA: Position Statement: gastric lavage. American Academy of Clinical Toxicology; European Association of Poisons Centres and Clinical Toxicologists. J Toxicol Clin Toxicol 1997; 35:711-719.
    380) Veena R, Narang APS, & Banday AW: Copper and zinc levels in maternal and fetal cord blood. Int J Gynecol Obstet 1991; 35:47-49.
    381) Viraraghavan T & Dronamraju MM: Removal of copper, nickel and zinc from wastewater by adsorption using peat. J Environ Sci Health A - Sci E 1993; 28:1261-1276.
    382) Vrzgula L, Bires J, & Hojerova A: The contents of heavy metals in the liver of ewes after experimentally induced intoxication by copperoxide from industrial air pollution (Czech). Vet Med (Prague) 1989; 34:297-306.
    383) Wahl PK, Lahiri P, & Mathur KS: Acute copper sulphate poisoning. J Assoc Phys India 1963; 11:93.
    384) Walker NI: Copper toxicosis in an Australian child. Eur J Med Res 1999; 4:249-251.
    385) Walker-Smith JA: Copper and the liver: late lessons from the Camperdown experience. Eur J Med Res 1999; 4:246-248.
    386) Walsh FM, Crosson FJ, & Bayley M: Acute copper intoxication. Am J Dis Child 1977; 131:149-151.
    387) Webb FTG: J Reprod Fertil 1973; 32:429-439.
    388) Wechsler LS, Checkoway H, & Franklin GM: A pilot study of occupational and environmental risk factors for Parkinson's disease. Neurotoxicol 1991; 12:387-392.
    389) Weeks JM, Jensen FB, & Depledge MH: Acid-base status, haemolymph composition and tissue copper accumulation in the shore crab Carcinus maenas exposed to combined copper and salinity stress. Mar Ecol - Progr Ser 1993; 97:91-98.
    390) Weis JS & Weis P: Trophic transfer of contaminants from organisms living by chromated-copper-arsenate (CCA)-treated wood to their predators. J Exp Mar Biol Ecol 1993; 168:25-34.
    391) Welsh PG, Skidmore JF, & Spry DJ: Effect of pH and dissolved organic carbon on the toxicity of copper to larval fathead minnow (Pimephales promelas) in natural lake waters of low alkalinity. Canad J Fisheries Aquat Sci 1993; 50:1356-1362.
    392) Winek CL, Collom WD, & Martineau P: Toluidine blue intoxication. Clin Toxicol 1969; 2:1-3.
    393) Witherell LE, Watson WN, & Giguere GC: Outbreak of acute copper poisoning due to soft drink dispenser (Letter). Amer J Pub Health 1980; 70:1115.
    394) Wohrl S, Kriechbaumer N, & Hemmer W: A cream containing the chelator DTPA diethylenetriaminepenta-acetic acid) can prevent contact allergic reactions to metals. Contact Dermatitis 2001; 44:224-228.
    395) Yang CC, Wu ML, & Deng JF: Severe hemolysis and methemoglobinemia in copper intoxication. J Toxicol - Clin Toxicol 1997; 35:521.
    396) Yang CC, Wu ML, Deng JF, et al: Prolonged hemolysis and methemoglobinemia following organic copper fungicide ingestion. Vet Human Toxicol 2004; 46:321-323.
    397) Yelin G, Taff ML, & Sadowski GE: Copper toxicity following massive ingestion of coins. Am J Forens Med Pathol 1987; 8:78-85.
    398) Yinon J & Zitrin S: The Analysis of Explosives. Pergamon Series in Analytical Chemistry, Vol 3, Pergamon Press, NY, New York, 1981, pp 2-135.
    399) Zacarias I, Yanez CG, & Araya M: Determination of the taste threshold of copper in water. Chem Senses 2001; 26:85-89.
    400) Zenz C: Occupational Medicine, 3rd ed, Mosby - Year Book, Inc, St. Louis, MO, 1994.
    401) Zimmerman HJ: Hepatotoxicity. The Adverse Effects of Drugs and Other Chemicals on the Liver, Appleton-Century-Crofts, New York, NY, 1978.
    402) Zuniga M, Vallejos P, Larrain A, et al: Toxicity of copper on four Chilean marine mussels. Bull Environ Contam Toxicol 2003; 71:1167-1174.
    403) do Nascimento TS, Pereira RO, de Mello HL, et al: Methemoglobinemia: from diagnosis to treatment. Rev Bras Anestesiol 2008; 58(6):651-664.