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PRINCIPLES OF TOXICOLOGY

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394 PROPERTIES AND EFFECTS <strong>OF</strong> ORGANIC SOLVENTS<br />

Elimination of methyl bromide is predominantly via the lungs as unchanged methyl bromide. A<br />

significant amount of methyl bromide, however, is metabolized in the body and may appear as inorganic<br />

bromide in the urine. “Normal” bromide ion concentration is below 1 mg/100 mL of blood serum, in<br />

the absence of the dietary sources (e.g., grains, beverages, medications). Five milligrams per 100 mL<br />

of blood may be considered evidence that exposure to bromide has occurred. If blood bromide is to<br />

be used in determining the exposure to methyl bromide, consideration must be given to other possible<br />

sources of bromide. The most common sources of inorganic bromide are medications, food, or water.<br />

Methylene chloride (see Figure 16.21) (or dichloromethane) is used as a common “blowing” agent<br />

for foams and as a solvent for many applications, including the coating of photographic films, in aerosol<br />

formulations, and to a large extent in paint processes, where its high degree of volatility is desirable.<br />

Owing to this volatility, high concentrations may be rapidly attained in poorly ventilated areas. It is a<br />

powerful solvent that is effective in dissolving cellulose esters, fats, oils, resins, and rubber. Methylene<br />

chloride is more water-soluble than most other chlorinated solvents.<br />

Methylene chloride is probably the least toxic of the four chlorinated methanes; the predominant<br />

toxic effect is CNS depression (expressed as narcosis). Other systemic effects in humans following<br />

nonlethal exposures to methylene chloride may include headache, giddiness, stupor, irritability,<br />

numbness, psychomotor disturbances, and increased carboxyhemoglobin levels. It is mildly irritating<br />

to the skin and dermal absorption is not considered a significant threat to human health unless massive<br />

concentrations are encountered. Eye contact may be painful but is not likely to cause serious injury.<br />

Adaptation to methylene chloride vapors occurs with repeated exposure, decreasing the ability to detect<br />

exposure.<br />

PHYSIOLOGIC RESPONSE TO METHYLENE CHLORIDE IN HUMANS<br />

Concentration (ppm) Response<br />

200–300 Odor threshold<br />

1000 Unpleasant odor level<br />

2300 Dizziness, fainting<br />

The symptoms of excessive exposure may be dizziness, nausea, tingling or numbness of the<br />

extremities, sense of fullness in the head, sense of heat, stupor, or dullness, lethargy, and drunkenness.<br />

Exposure to sufficiently high concentrations of methylene chloride may lead to rapid unconsciousness<br />

and death. Prompt removal from exposure area typically results in complete recovery.<br />

Historical industrial experience with methylene chloride has been remarkably free of serious<br />

adverse effects. Nephrotoxic and hepatotoxic potential of methylene chloride is considered low under<br />

typical industrial environments. Reports of systemic injury are rare and, although dermatitis has been<br />

reported because of common usage in paint remover formulations, only a few anesthetic deaths have<br />

occurred, all at extreme concentrations. Methylene chloride is known to be metabolized to carbon<br />

monoxide, but symptoms of carbon monoxide poisoning, such as headaches, have not been a common<br />

feature of methylene chloride reports. This indicates that carboxyhemoglobin levels alone are not a<br />

good measure of the toxic effect of methylene chloride. Acute exposures have resulted in liver or kidney<br />

Figure 16.21 Methylene chloride.

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