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DƯỢC LÍ Goodman & Gilman's The Pharmacological Basis of Therapeutics 12th, 2010

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Toxicity to the nervous system is the primary concern

with chronic exposure to mercury vapor. Mercury

vapor induces characteristic CNS symptoms that are

consistent across patients exposed to mercury over short

or long periods. These symptoms include tremors (particularly

of the hands), emotional lability (irritability,

shyness, loss of confidence, and nervousness), insomnia,

memory loss, muscular atrophy, weakness, paresthesia,

and cognitive deficits. These symptoms intensify

and become irreversible, with increases in duration and

concentration of exposure. Other common symptoms of

chronic mercury exposure include tachycardia, labile

pulse, severe salivation, and gingivitis. Prolonged exposure

to mercury also causes kidney damage.

Inorganic Salts of Mercury. Ingestion of Hg 2+ salts is

intensely irritating to the GI tract, leading to vomiting,

diarrhea, and abdominal pain. The kidney is the primary

target of both valence states of inorganic mercury.

Acute exposure to mercury salts (typically in suicide

attempts) leads to tubular necrosis, resulting in

decreased urine output and often acute renal failure.

Chronic exposures also target the kidney, with glomerular

injury predominating.

Organic Mercury. The CNS is the primary target of

methyl mercury toxicity. Two incidents of high-dose

exposure to methyl mercury provide much of our

knowledge regarding methyl mercury poisoning. One

was in fishing villages surrounding the heavily polluted

Minamata Bay in Japan, and the other was in Iraq,

where grains treated with methyl mercury were accidentally

consumed. Symptoms of methyl mercury

exposure include visual disturbances, ataxia, paresthesia,

fatigue, hearing loss, slurring of speech, cognitive

deficits, muscle tremor, movement disorders, and, following

severe exposure, paralysis and death. The developing

nervous system exhibits increased sensitivity to

methyl mercury. Children exposed in utero can develop

severe symptoms, including mental retardation and

neuromuscular deficits, even in the absence of symptoms

in the mother. In adults, methyl mercury causes

focused lesions in specific areas of the brain, while the

brains of children exposed in utero sustain widespread

damage (Clarkson, 2002).

The effects of low-dose methyl mercury exposure from routine

consumption of fish are difficult to assess due to the opposing

beneficial effects of -3 fatty acids found in fish oils, and studies

have produced discrepant results (Grandjean et al., 1999; Myers

et al., 2003; Myers et al., 2007).

Treatment. With exposure to metallic mercury, termination of exposure

is critical and respiratory support may be required. Emesis may

be used within 30-60 minutes of exposure to inorganic mercury, provided

the patient is awake and alert and there is no corrosive injury.

Maintenance of electrolyte balance and fluids is important for patients

exposed to inorganic mercury. Chelation therapy is beneficial in

patients with acute inorganic or metallic mercury exposure. There are

limited treatment options for methyl mercury. Chelation therapy does

not provide clinical benefits, and several chelators potentiate the toxic

effects of methyl mercury (Rush, 2008). Nonabsorbed thiol resins may

be beneficial by preventing reabsorption of methyl mercury from the

GI tract.

Because of the conflicting effects of mercury and -3 fatty

acids, there is considerable controversy regarding the restriction of

fish intake in women of reproductive age and children. The EPA recommends

limiting fish intake to 12 oz (two meals) per week. Many

experts feel this recommendation is too conservative, and the FDA

is considering revising their recommendation to state that the benefits

of fish consumption outweigh the risks. The recommendation

that women consume fish that is lower in mercury content (i.e.,

canned light tuna, salmon, pollock, catfish) and avoid top predators,

such as swordfish, shark, and tilefish, is not controversial.

Arsenic

Arsenic is a metalloid that is common in rocks and soil.

Arsenic compounds have been used for >2400 years as

both therapeutic agents and poisons. In the late 19th

century, Robert Ehrlich coined the terms “magic bullet”

and “chemotherapy” to describe his work using the

organic arsenic compound arsphenamine for the treatment

of syphilis. The use of arsenic in drugs has been

mostly phased out, but arsenic trioxide (ATO) is still

used as an effective chemotherapy agent for acute

promyelocytic leukemia (see Chapter 63).

Exposure. The primary source of exposure to arsenic is through drinking

water. Arsenic naturally leaches out of soil and rocks into well

and spring water (Mead, 2005). Levels of arsenic in drinking water

average 2 μg/L (ppb) in the U.S. but can be >50 μg/L (five times the

EPA standard) in private well water, particularly in California,

Nevada, and Arizona. Drinking water from other parts of the world

where well water has been promoted to prevent waterborne illness,

particularly Taiwan, China, Argentina, Chile, Bangladesh, and eastern

India, sometimes is contaminated with much higher levels of

arsenic (sometimes several hundred micrograms per liter), and

widespread poisonings have resulted (Figure 67–8). Studies in

Bangladesh found that ~40% of water samples from across the country

were contaminated with >50 μg/L of arsenic, and some samples

had far higher levels (Mead, 2005; Chowdhury et al., 1999; BGS and

DPHE, 2001). Arsenic also can enter the environment through human

activities such as the use of arsenic-containing pesticides, mining,

and burning of coal. Food, particularly seafood, often is contaminated

with arsenic. Arsenic in seafood exists primarily as organic compounds

(i.e., arsenobetaine) that are much less toxic than inorganic

arsenic. The average daily human intake of arsenic is 10 μg/day,

almost exclusively from food and water.

Before 2003, >90% of arsenic used in the U.S. was as a

preservative in pressure-treated wood, but the lumber industry has

1867

CHAPTER 67

ENVIRONMENTAL TOXICOLOGY: CARCINOGENS AND HEAVY METALS

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