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hexachlorobutadiene - Davidborowski.com

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HEXACHLOROBUTADIENE 60<br />

2. HEALTH EFFECTS<br />

<strong>hexachlorobutadiene</strong>-induced renal damage. Similar results were reported in tests evaluating MFO<br />

inducers such as phenobarbital (Lock and Ishmael 1981), β-naphthoflavone, isosafrole, and Aroclor<br />

1254 (Hook et al. 1982). Renal toxicity was not exacerbated by prior exposure to ketonic solvents<br />

(Hewitt and Brown 1984).<br />

There are reports of interactions of <strong>hexachlorobutadiene</strong> with other chemicals. Combined<br />

administration of minimally toxic doses of <strong>hexachlorobutadiene</strong> with mercuric chloride and potassium<br />

dichromate for 24 hours caused synergistic effects as evident by marked increases in urinary<br />

(6-24 hour) alkaline phosphatase, lactate dehydrogenase and N-acetyl-β-glucosaminidase activities, as<br />

well as more severe tubular necrosis than caused by treatment with <strong>hexachlorobutadiene</strong> alone (Jonker<br />

et al. 1993a). Antagonistic effects were evident as characterized by smaller increases in urinary γ-glutamyl<br />

transferase activity <strong>com</strong>pared to treatment with <strong>hexachlorobutadiene</strong> alone. Combined<br />

administration of the same chemicals did not cause additive interactions regarding biochemical<br />

parameters or histopathological changes in the kidney (Jonker et al. 1993a). An additional study<br />

revealed that when animals are treated for 4 weeks with minimally toxic doses of <strong>hexachlorobutadiene</strong><br />

in <strong>com</strong>bination with other chemicals (mercuric chloride, δ-limonene, and lysinoalanine), there is an<br />

increase in growth retardation and renal toxicity (renal weight, urine concentrating ability, and renal<br />

structure) in male rats but not in females (Jonker et al. 1993b).<br />

2.7 POPULATIONS THAT ARE UNUSUALLY SUSCEPTIBLE<br />

A susceptible population will exhibit a different or enhanced response to <strong>hexachlorobutadiene</strong> than<br />

will most persons exposed to the same level of <strong>hexachlorobutadiene</strong> in the environment. Reasons<br />

include genetic make-up, developmental stage, age, health and nutritional status (including dietary<br />

habits that may increase susceptibility, such as inconsistent diets or nutritional deficiencies), and<br />

substance exposure history (including smoking). These parameters result in decreased function of the<br />

detoxification and excretory processes (mainly hepatic, renal, and respiratory) or the pre-existing<br />

<strong>com</strong>promised function of target organs (including effects or clearance rates and any resulting endproduct<br />

metabolites). For these reasons we expect the elderly with declining organ function and the<br />

youngest of the population with immature and developing organs will generally be more vulnerable to<br />

toxic substances than healthy adults. Populations who are at greater risk due to their unusually high<br />

exposure are discussed in Section 5.6, Populations With Potentially High Exposure.

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