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Metabolism of halogenated ethylenes.

The metabolism of the chlorinated ethylenes may be explained by the formation of chloroethylene epoxides as the first intermediate products. The evidence indicates that these epoxides rearrange with migration of chlorine to form chloroacetaldehydes and chloroacetyl chlorides. Thus, monochloroacetic acid, chloral hydrate, and trichloroacetic acid have been found in reaction mixtures of 1,1-dichloroethylene, trichloroethylene, and tetrachloroethylene, respectively, with rat liver microsomal systems. Rearrangements of the chloroethylene, and glycols formed from the epoxides by hydration may also take place, but would appear, at least in the case of 1,1-dichloroethylene, to be quantitatively less important. The literature on the metabolism of chlorinated ethylenes and its relationship to their toxicity is reviewed.

Animals↗

Clinical evaluation of liver structure and function in humans exposed to halogenated hydrocarbons.

An unresolved question is whether humans exposed to comparatively low doses of persistent environmental chemicals such as polyhalogenated biphenyls or organochlorine pesticides are at risk for injury to the liver. Cross-sectional epidemiologic studies suggest that these chemicals may produce statistically significant but clinically mild abnormalities in the commonly employed chemical tests of liver function. The few reports of human liver morphology reveal nonspecific changes reflecting effects of lipophilic chemicals. There is evidence that chemicals of this category in at least some doses cause induction of liver microsomal enzymes involved in biotransformation of foreign substances. This finding has been documented by measurements of the clearance of model drugs or the appearance in the urine of steroid metabolites or glucaric acid. Although a positive statistical correlation between the concentrations of these chemicals in serum and the serum gamma-glutamyltranspeptidase activity has been reported, the non-specificity of the latter enzyme precludes conclusion that this change is indicative of induction of liver microsomal enzymes. Although the effects of this type of environmental chemical are not indicative of progressive liver disease, only prospective clinical trials can resolve the issue of the risk for future development of liver malignancy.

Chlordecone↗

Model studies in cytochrome P-450-mediated toxicity of halogenated compounds: radical processes involving iron porphyrins.

Haloalkane toxicity originates from attack on biological targets by reactive intermediates derived from haloalkane metabolism by a hemoprotein, cytochrome P-450. Carbon-centered radicals and their peroxyl derivatives are most likely involved. The reactions of iron porphyrin--a model for cytochrome P-450--with various carbon-centered and peroxyl radicals generated by pulse radiolysis are examined. Competition between iron porphyrin and unsaturated fatty acids for attack by peroxyl radicals is pointed out. These kinetic data are used to derive a model for toxicity of haloalkanes with particular attention to carbon tetrachloride and halothane. The importance of local oxygen concentration and structural arrangement of fatty acids around cytochrome P-450 is emphasized.

Animals↗

Impact of halogenated compounds on calcium homeostasis in hepatocytes.

Halocarbons (CCl4, 1,1-dichlorethylene) cause a wide spectrum of effects and injury in hepatocytes. One early effect of these compounds is the inhibition and destruction of the endoplasmic reticulum (ER) calcium pump. Subsequent to inhibition of this pump, the ER calcium pool is depleted and cytosolic levels of calcium are increased for a prolonged period of time. This effect of halocarbons has been characterized and is similar in vivo and in vitro. The importance of this redistribution of cell calcium in expression of halocarbon injury of hepatocytes has not been fully resolved. Several degradative enzymes (phospholipases, proteases) have been implicated as calcium-dependent mediators in toxicity. Our preliminary studies of the effect of calcium redistribution suggest that activation of a calcium-sensitive endonuclease in liver does not play a central role in initiating the lethal effect of halocarbons on hepatocytes.

Animals↗

Studies on the mechanism of nephrotoxicity and nephrocarcinogenicity of halogenated alkenes.

There is now a considerable weight of evidence from studies in a number of different laboratories with different haloalkenes to suggest that these compounds undergo conjugation with glutathione followed by degradation of the S-conjugate (Figure 1) to produce cytotoxic, and in some cases mutagenic, metabolites. These effects are dependent upon the sequential metabolism by gamma-glutamyl transferase and dipeptidases to produce the cysteine conjugates, and the presence of renal transport systems which concentrate the chemical in renal cells. These conjugates then appear to undergo further metabolism to a reactive thiol by the renal enzyme cysteine-conjugate beta-lyase, a process which can be blocked by inhibiting the enzyme with AOAA. Renal beta-lyase is present in both the cytosol and mitochondrial fractions, but toxicity studies in isolated cells and mitochondria indicate that the primary mode of action of these compounds is the inhibition of mitochondrial respiration, suggesting that the mitochondrial beta-lyase may be more important than the cytosolic enzyme in cysteine S-conjugate bioactivation. In addition to the renal cell injury caused by the presumed reactive thiol metabolite, reaction with DNA also occurs as the chlorinated, but not fluorinated, analogs are mutagenic, and in the case of HCBD, carcinogenic. Thus the target organ, cellular and subcellular specificity of haloalkene-S-conjugates, is due to the presence of bioactivating enzymes and the susceptibility of certain biochemical processes. The precise relationship between (1) the mitochondrial effects and cytotoxicity and (2) the interaction of the chemical with DNA and its mutagenicity require more precise understanding in order to elucidate the mechanism of S-conjugate-induced cell death and carcinogenicity. The routes and rates of metabolism of some of these compounds, with respect to glutathione conjugation vs. oxidative metabolism, in both experimental animals and man are required to help assess the risk associated with this class of chemicals.

Alkenes↗