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The most common inorganic trivalent arsenic compounds are arsenic trioxide and sodium arsenite, whereas common pentavalent inorganic compounds are sodium arsenate, arsenic pentoxide, and arsenic acid. Important organo-arsenicals include arsenilic acid, arsenosugars, and several methylated forms produced as a consequence of inorganic arsenic biotransformation in various organisms, including humans. Arsine (AsH3) is an important gaseous arsenical.
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Occupational exposure to arsenic occurs in the manufacture of pesticides, herbicides, and other agricultural products. High exposure to arsenic fumes and dusts may occur in smelting industries. Environmental arsenic exposure mainly occurs from arsenic-contaminated drinking water, which is often from natural sources. Environmental exposure to arsenic also occurs from burning of coal containing naturally high levels of arsenic. Food, especially seafood, may contribute significantly to daily arsenic intake.
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Ingestion of large doses (70 to 180 mg) of inorganic arsenic can be fatal. Symptoms of acute intoxication include fever, anorexia, hepatomegaly, melanosis, cardiac arrhythmia, and, in fatal cases, eventual cardiac failure. Acute arsenic ingestion can damage mucous membranes of the gastrointestinal tract, causing irritation, vesicle formation, and even sloughing. Sensory loss in the peripheral nervous system is the most common neurological effect, appearing at 1 to 2 weeks after large doses and consisting of Wallerian degeneration of axons. Anemia and leucopenia, particularly granulocytopenia, occur a few days following high-dose arsenic exposure and are reversible.
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The skin is a major target organ in chronic inorganic arsenic exposure. Skin cancer is common with protracted high-level arsenical exposure. Liver injury, characteristic of long-term or chronic arsenic exposure, manifests itself initially as jaundice, abdominal pain, and hepatomegaly and may progress to cirrhosis and ascites, even to hepatocellular carcinoma.
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Repeated exposure to low levels of inorganic arsenic can produce peripheral neuropathy. This neuropathy usually begins with sensory changes, such as numbness in the hands and feet, but later may develop into a painful “pins and needles” sensation. Both sensory and motor nerves can be affected, and dying-back axonopathy with demyelination may occur.
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Mechanisms of Toxicity
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The trivalent compounds of arsenic are the principal toxic forms and pentavalent arsenate is an uncoupler of mitochondrial oxidative phosphorylation. Arsenic and its metabolites have been shown to produce oxidants and oxidative DNA damage, alteration in DNA methylation status and genomic instability, impaired DNA damage repair, and enhanced cell proliferation.
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Arsenic is a known human carcinogen, associated with tumors of the skin, lung, and urinary bladder, and possibly kidney, liver, and prostate. Arsenic-induced skin cancers include basal cell carcinomas and squamous cell carcinomas, both arising in areas of arsenic-induced hyperkeratosis. In humans, increased mortality occurs from lung cancer in young adults following in utero exposure to arsenic. Thus, the developing fetus appears to be hypersensitive to arsenic carcinogenesis.
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For acute arsenic poisoning, treatment is symptomatic, with particular attention to fluid volume replacement and support of blood pressure. The oral chelator penicillamine or succimer (2,3-dimercaptosuccinic acid, DMSA) is effective in removing arsenic from the body. For chronic poisoning, che-lator therapy has not proven effective in relieving symptoms. The best strategy for preventing chronic arsenic poisoning is by reducing exposure.
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About 75 percent of cadmium produced is used in batteries, especially nickel–cadmium batteries. Because of its noncorrosive properties, cadmium has been used in electroplating or galvanizing alloys for corrosion resistance. It is also used as a color pigment for paints and plastics. This metal is produced as a byproduct of zinc and lead smelting.
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Food is the major source of cadmium for the general population. Many plants readily accumulate cadmium from soil. Both natural and anthropogenic sources of cadmium contamination occur for soil, including fallout of industrial emissions, some fertilizers, soil amendments, and use of cadmium-containing water for irrigation, all resulting in a slow but steady increase in the cadmium content in vegetables over the years. Shellfish and animal liver and kidneys can accumulate relatively high levels of cadmium. Air can be a significant source of direct exposure or environmental contamination. Cigarette smoking is a major nonoccupational source of cadmium exposure.
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Inhalation is the dominant route of exposure in occupational settings. Occupations potentially at risk from cadmium exposure include those involved with refining zinc and lead ores, iron production, cement manufacture, industries involving fossil fuel combustion, the manufacturing of paint pigments, cadmium–nickel batteries, and electroplating.
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Acute toxicity from the ingestion of high concentrations of cadmium in the form of heavily contaminated beverages or food causes severe irritation to the gastrointestinal epithelium, leading to nausea, vomiting, and abdominal pain. Inhalation of cadmium fumes or other heated cadmium-containing materials may produce acute pneumonitis with pulmonary edema.
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The major long-term toxic effects of low-level cadmium exposure are renal injury, obstructive pulmonary disease, osteoporosis, and cardiovascular disease. Cancer is primarily a concern in occupationally exposed groups. The chronic toxic effects of cadmium are clearly a much greater concern than the rare acute toxic exposures.
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Cadmium is toxic to tubular cells and glomeruli, markedly impairing renal function leading to proteinuria. These lesions consist of initial tubular cell necrosis and degeneration, progressing to an interstitial inflammation and fibrosis. Because of the potential for renal toxicity, there is considerable concern about the levels of dietary cadmium intake for the general population.
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Chronic Pulmonary Disease
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Cadmium inhalation is toxic to the respiratory system in a fashion related to the dose and duration of exposure. Cadmium-induced obstructive lung disease in humans can be slow in onset, and results from chronic bronchitis, progressive fibrosis of the lower airways, and accompanying alveolar damage leading to emphysema. Pulmonary function is reduced with dyspnea, reduced vital capacity, and increased residual volume.
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Cadmium toxicity affects calcium metabolism, and associated skeletal changes probably related to calcium loss include bone pain, osteomalacia, and/or osteoporosis. Epidemiologic studies suggest that cadmium may be an etiologic agent for essential hypertension. Heart mitochondria may be the site of the cadmium-induced reduction in myocardial contractility. Epidemiologic studies in humans have suggested a relationship between abnormal behavior and/or decreased intelligence in children and adults exposed to cadmium.
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Lead is a ubiquitous toxic metal and is detectable in practically all phases of the inert environment and in all biological systems. The phasing out of leaded gasoline and the removal of lead from paint, solder, and water supply pipes have significantly lowered blood lead levels in the general population. Lead exposure in children still remains a major health concern.
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Lead-containing paint is a primary source of lead exposure in children. Major environmental sources of lead for infants and toddlers up to 4 years of age are hand-to-mouth transfer of lead-containing paint chips and dust from floors of older housing. Lead in household dust can also come from outside of the home (i.e., soil). A major route of exposure for the general population is from food and water. Dietary intake of lead has decreased dramatically in recent years. Other potential sources of lead exposure are recreational shooting, hand-loading ammunition, soldering, jewelry making, pottery making, gun smithing, glass polishing, painting, and stained glass crafting.
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The toxic effects of lead and the minimum blood level at which an effect is likely to be observed are shown in Table 23–1 Lead can induce a wide range of adverse effects in humans depending on the dose and duration of exposure. The toxic effects range from inhibition of enzymes to the production of severe pathology or death. Children are most sensitive to effects in the central nervous system, whereas peripheral neuropathy, chronic nephropathy, and hypertension are concerns in adults. Other target tissues include the gastrointestinal, immune, skeletal, and reproductive systems. Effects on the heme biosynthesis provide a sensitive biochemical indicator even in the absence of other detectable effects.
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Neurologic, Neurobehavioral, and Developmental Effects in Children
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Symptoms of lead encephalopathy begin with lethargy, vomiting, irritability, loss of appetite, and dizziness, progressing to obvious ataxia, and a reduced level of consciousness, which may progress to coma and death. Recovery is often accompanied by sequelae including epilepsy, mental retardation, and, in some cases, optic neuropathy and blindness.
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The most sensitive indicators of adverse neurologic outcomes are psychomotor tests or mental development indices, and broad measures of IQ. Lead may act as a surrogate for calcium and/or disrupt calcium homeostasis. The stimulation of protein kinase C may result in alteration of the blood–brain barrier. Lead affects virtually every neurotransmitter system in the brain, including glutamatergic, dopaminergic, and cholinergic systems. All these systems play a critical role in synaptic plasticity and cellular mechanisms for cognitive function, learning, and memory.
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Neurotoxic Effects in Adults
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Adults with occupational exposure may demonstrate abnormalities in a number of measures in neurobehavior. Peripheral neuropathy is a classic manifestation of lead toxicity in adults. Footdrop and wristdrop may be observed in workers with excessive occupational exposure to lead. Peripheral neuropathy is characterized by segmental demyelination and possibly axonal degeneration.
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Lead has multiple hematologic effects, ranging from increased urinary porphyrins, coproporphyrins, δ-aminolevulinic acid (ALA), and zinc-protoporphyrin to anemia. The heme biosynthesis pathway and the sites of lead interference are shown in Figure 23–2. The most sensitive effects of lead are the inhibition of δ-aminolevulinic acid dehydratase (ALAD) and ferrochelatase. ALAD catalyzes the condensation of two units of ALA to form phorphobilinogen (PBG). Inhibition of ALAD results in accumulation of ALA. Ferrochelatase catalyzes the insertion of iron into the protoporphyrin ring to form heme. Inhibition of ferrochelatase results in accumulation of protoporphyrin IX, which takes the place of heme in the hemoglobin molecule and, as the erythrocytes containing protoporphyrin IX circulate, zinc is chelated at the site usually occupied by iron. Anemia only occurs in very marked cases of lead toxicity.
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Acute lead nephrotoxicity consists of proximal tubular dysfunction and can be reversed by treatment with chelating agents. Chronic lead nephrotoxicity consists of interstitial fibrosis and progressive nephron loss, azotemia, and renal failure. Lead nephrotoxicity impairs the renal synthesis of heme-containing enzymes in the kidney, such as heme-containing hydroxylase involved in vitamin D metabolism causing bone effects. Hyperuricemia with gout occurs more frequently in the presence of lead nephropathy.
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Effects on Cardiovascular System
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The pathogenesis of lead-induced hypertension is multifactorial including: (1) inactivation of endogenous nitric oxide and cGMP, possibly through lead-induced reactive oxygen species; (2) changes in the renin–angiotensin–aldosterone system, and increases in sympathetic activity, important humoral components of hypertension; (3) alterations in calcium-activated functions of vascular smooth muscle cells including contractility by decreasing Na+/K+-ATPase activity and stimulation of the Na+/Ca2+ exchange pump; and (4) a possible rise in endothelin and thromboxane.
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Lead may affect blood pressure via changes in plasma renin and in urinary kallikrein, alterations in calcium-activated functions of vascular smooth muscle cells, and changes in responsiveness to catecholamines. As an immunosuppressive agent, lead decreases immunoglobulins, peripheral B lymphocytes, and other components of the immunologic system. Retention and mobilization of lead in bone occur by the same mechanisms involved in regulating calcium influx and efflux. Lead also competes with calcium for gastrointestinal absorption. Lead is known to affect osteoblasts, osteoclasts, and chrondrocytes and has been associated with osteoporosis and delays in fracture repair. Lead toxicity has long been associated with sterility and neonatal deaths in humans. Lead, a 2B carcinogen, induces tumors of the respiratory and digestive systems. Epidemiologic studies suggest a relationship between occupational lead exposure and cancer of the lung, brain, and bladder among workers exposed to lead.
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Also called quicksilver, metallic mercury is in liquid state at room temperature. Mercury vapor (Hg0) is much more hazardous than the liquid form. Mercury binds to other elements (such as chlorine, sulfur, or oxygen) to form inorganic mercurous (Hg+) or mercuric (Hg2+) salts.
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Global Cycling and Ecotoxicology
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Mercury exemplifies movement of metals in the environment (Figure 23–3). Atmospheric mercury, in the form of mercury vapor (Hg0), is derived from natural degassing of the earth's crust and through volcanic eruptions as well as from evaporation from oceans and soils. Anthropogenic sources have become a significant contributor to atmospheric mercury. These include emissions from metal mining and smelting (mercury, gold, copper, and zinc), coal combustion, municipal incinerators, and chloralkali industries. Methylmercury enters the aquatic food chain starting with plankton, then herbivorous fish, and finally ascending to carnivorous fish and sea mammals. On the top of the food chain, tissue mercury can rise to levels 1800 to 80,000 times higher than levels in the surrounding water. This biomethylation and bioconcentration result in human exposure to methylmercury through consumption of fish.
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Consumption of fish is the major route of exposure to methylmercury. Inorganic mercury compounds are also found in food. The source of inorganic mercurial is unknown but the amounts ingested are far below known toxic levels. Mercury in the atmosphere and in drinking water is generally so low that it does not constitute an important source of exposure to the general population.
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Occupational Exposure
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Inhalation of mercury vapor may occur from working in the chloralkali industry. Occupational exposure may occur during manufacture of a variety of scientific instruments and electrical control devices, in dentistry where mercury amalgams are used in tooth restoration, and in the extraction of gold.
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Elemental mercury exposure can occur from broken elemental mercury containers, medicinal devices, barometers, and melting tooth amalgam fillings to recover silver. Inhalation of large amounts of mercury vapor can be deadly.
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Inhalation of mercury vapor at extremely high concentrations may produce an acute, corrosive bronchitis and interstitial pneumonitis and, if not fatal, may be associated with central nervous system effects such as tremor or increased excitability. This condition has been termed the asthenic-vegetative syndrome or micromercurialism. Identification of the syndrome requires neurasthenic symptoms and three or more of the following clinical findings: tremor, enlargement of the thyroid, increased uptake of radioiodine in the thyroid, labile pulse, tachycardia, dermographism, gingivitis, hematologic changes, or increased excretion of mercury in urine.
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The kidney is the major target organ for inorganic mercury. Although a high dose of mercuric chloride is directly toxic to renal tubular cells, chronic low-dose exposure to mercury salts may induce an immunologic glomerular disease. Exposed persons may develop proteinuria that is reversible after they are removed from exposure.
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The major human health effect from exposure to methylmercury is neurotoxicity. Clinical manifestations of neurotoxicity include paresthesia (a numbness and tingling sensation around the mouth and lips) and ataxia, manifested as a clumsy, stumbling gait, and difficulty in swallowing and articulating words. Other signs include neurasthenia (a generalized sensation of weakness), vision and hearing loss, and spasticity and tremor. These may finally progress to coma and death. The overall acute effect is cerebral edema, but with prolonged destruction of gray matter and subsequent gliosis, cerebral atrophy results.
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Mechanism of Toxicity
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High-affinity binding of divalent mercury to sulfhydryl groups of proteins in the cells is an important mechanism for producing nonspecific cell injury or even cell death. Other general mechanisms, such as the interruption of microtubule formation, inhibition of enzymes, oxidative stress, interruption of protein and DNA synthesis, and autoimmune responses, have also been proposed. Mercury causes overexpression of metallothionein and glutathione system-related genes in rat tissues.
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Metallic nickel is produced from sulfide and silicate-oxide ores. Nickel is used in various metal alloys, including stainless steels, and in electroplating. Occupational exposure to nickel occurs by inhalation of nickel-containing aerosols, dusts, or fumes, or dermal contact in workers engaged in nickel production (mining, milling, refinery, etc.) and nickel-using operations (melting, electroplating, welding, nickel–cadmium batteries, etc.). Nickel is ubiquitous in nature, and the general population is exposed to low levels of nickel in air, cigarette smoke, water, and food.
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Nickel-induced contact dermatitis is the most common adverse health effect from nickel exposure and is found in 10 to 20 percent of the general population. It can result from exposure to airborne nickel, liquid nickel solutions, or prolonged skin contact with metal items containing nickel, such as coins and jewelry.
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Nickel Carbonyl Poisoning
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Nickel carbonyl is extremely toxic. Intoxication begins with headache, nausea, vomiting, and epigastric or chest pain, followed by cough, hyperpnea, cyanosis, gastrointestinal symptoms, and weakness. The symptoms may be accompanied by fever and leukocytosis. More severe cases can progress to pneumonia, respiratory failure, and eventually to cerebral edema and death.
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Nickel is a respiratory tract carcinogen in nickel-refining industry workers. Risks are highest for lung and nasal cancers among workers heavily exposed to nickel sulfide, nickel oxide, and metallic nickel.