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', • • <br /> <br />I , <br /> <br /> <br /> <br />i~ <br /> <br /> <br /> <br /> <br /> <br /> <br /> <br /> <br /> <br /> <br /> <br />ential ultraviolet irradiation (Kelada 1989); differ- <br />ential pulse polarography (Westly 1988); and <br />modified spectrophotometric (Blago 1989; Ohno <br />1989), colorometric (Lundquist and Sorbo 1989), <br />and ion chromatographic determinations (Nono- <br />mura and Hobo 1989). Analysis of cyanide and <br />cytochrome oxidase is usually conducted with sam- <br />ples of whole blood, serum, plasma, brain, or ven- <br />tricular myocardium tissues. Samples should be <br />obtained as soon as possible after cyanide exposure <br />and analyzed immediately, otherwise erroneous <br />analytical values will result (Tow•ill et a1. 1978; <br />Ballantyne 1983). Brain and liver are recom- <br />mended for cyanide analysis if removed and ana- <br />lyzed within a week (Ballantyne et al. 1974). <br />Cyanide measurements are further confounded by <br />the presence of various antidotal agents (Ballan- <br />tyne 19831; by v;;rious tissue presen•atives, such <br />as formaldoxime (Knocke 1981) and sodium fluo- <br />ride (Curry et al. 1967); and by the spontan- <br />eous postmortem production of cyanide in various <br />tissues (e.g., sterile blood, brain, liver, kidney, <br />uterus, intestines) over time in cases of noncyani de <br />death (Curry et al. 1967; Ballantyne et al. 1974). <br />Mode of Action <br />Cyanide is a potent and rapid-acting asphyxi- <br />ant. At lethal doses, inhalation or ingestion of cya- <br />nide produces reactions within seconds and death <br />within minutes. Cyanide's toxic effect is due to its <br />affinity for the ferric heme form of cytochrome aa, <br />also known as cytochrome c oxidase, the terminal <br />oxidase of the mitochondria] respiratory chain <br />(Towill et al. 1978; Egekeze and Oehme 1980; <br />Solomonson 1981; Way 1981, 1984; Leduc et al. <br />1982; Biehl 1984; Ballantyne 1987a; Marrs and <br />Ballantyne 1987; Yamamoto 1989). Inhibition of <br />the enzyme c}~tochrome c oxidase is thought Co in- <br />volve atwo-step reaction-initial penetration of <br />cyanide into s protein crevice followed by binding <br />to heme iron. Formation of a stable cvtochrome c <br />oxidase-CN complex in the mitochondria produces <br />a blockage of electron transfer from c}~tochrome <br />oxidase to molecular oxygen and cessation of cellu- <br />3ar respiration, causing cytotoxic h}•poxia in the <br />presence of normal hemoglobin oxygenation. Tis- <br />sueanoxia induced by the activation of cvtochrome <br />oxidase causes a shift from aerobic to anaerobic <br />metabolism, resulting in the depletion of energ}- <br />rich compounds such as glycogen, phosphocrea- <br />tine,and adenosine triphosphate, and the accumu- <br />CYANIDE <br />lation of lactate with decreased blood pH. The com- <br />bination of cytotoxic hypoxia with lactate acidosis <br />depresses the central nervous system-the most <br />sensitive site of anoxia-resulting in respiratory <br />arrest and death. If the absorption rate is signifi- <br />cantly greater than the detoxification rate, there <br />will be a rapid accumulation of free cyanide in tis- <br />sues and body fluids, resulting in the prompt onset <br />of signs of acute cyanide poisoning. Acute cyanide <br />poisoning is frequently encountered as a relatively <br />massive overdose, where the amqunt of cyanide <br />greatly exceeds the minima] conceptration neces- <br />sary toinhibit cytochrome coxidase. Insuch cases, <br />many enzymes and biological systems are dis- <br />rupted. includingvarious metalloegzymes,nitrate <br />reductase, nitrite reductase, myo~lobin, various <br />peroxidases, catalase, and ribulose diphosphate <br />carboxylase, resulting in severe signs of toxicity <br />and rapid death. <br />The great majority of the absorbed cyanide re- <br />acts with thiosultate in the presence of enzymes to <br />produce thiocyanate, which is excreted in the urine <br />over a period of several days. Owing to this rapid <br />detoxification, animals can ingest high sublethal <br />doses of cyanide over extended periods without <br />harm (Towil] et al. 1978; Egekeze and Oehme <br />1980; EPA 1980; Davis 1981; Solorttonson 1981; <br />Leduc 1989; Ballantyne 1987a; Oh et al. 1987; <br />Marrs and Ballantyne 1987; Westley 1988; Mengel <br />et al. 1989). Authorities are also in general agree- <br />ment on several points: thiosultate iS usually low <br />in the body, and higher levels can sigrzoficantly pro- <br />tectagainstcyanidetoxicity;species v&ryconsider- <br />ably in both the extent to which thiocyanate is <br />formed and the rate at which it is elitriinated from <br />the body; thiocyanate metabolites resulting from <br />the transulfuration process are about 120 times <br />less toxic than the parent cyanide compound; <br />thiocyanate may accumulate in tissues and has <br />been associated with developmental abnormalities <br />and other adverse effects; the two enzyme sys- <br />tems responsible for the transulfuratlion process <br />are thiosultate-cyanide sulfurtransfkrase-also <br />known as rhodanese-and beta-mercaptopvru- <br />vate cyanide sulfurtransCerase. Rhpdanese is <br />widely distributed in the body, but acflivity levels <br />in mammals are highest in the mitochondria] frac- <br />tion of liver. Rhodanese activity levels in catalyz- <br />ing the transformation of thiosultate to thio- <br />cyanate are limited by the availability aCsulfur. <br />Minor detoxification pathways for cyanide in- <br />clude exhalation in breath as HCN and as CO: <br />from oxidative metabolism of formic acid; conjuga- <br />tion with cystine to form 2-iminothiazolidene- <br />