Saleh M A
Environmental Research Center, University of Nevada-Las Vegas 89154.
Rev Environ Contam Toxicol. 1991;118:1-85. doi: 10.1007/978-1-4612-3082-3_1.
The chemistry of toxaphene is now well developed; 20 isomers have been isolated and identified. The molecular weight and molecular formula are known for the remaining major components. The major metabolic degradation mechanisms for toxaphene in all organisms from bacteria to primates are now believed to the reductive dechlorination, reductive dehydrochlorination, and in some cases, oxidative dechlorination to produce hydroxyl derivatives, acids or ketones. Earlier reports that toxaphene was biodegradable were published before the advent of state-of-the-art analytical methodology which has permitted detection at levels in the range of ppb. Toxaphene residues have recently been documented throughout the biosphere as well as in human milk, even though its use was banned in 1982. This global persistence is against previous beliefs that toxaphene was easily biodegradable. During the last decade advances have been achieved in the selectivity, accuracy, and sensitivity of detection techniques so that the presence of toxaphene throughout the biosphere has been extensively documented. Through the use of GC/MS and electron capture GC, toxaphene can now be detected at ppb levels, making possible a more consistent and accurate assessment of the compound's presence in organisms as well as in soil, water, and ground water. Toxaphene residues have been detected in human populations, fish and wildlife, soil, water, and ground water as well as in food. An FDA Food Survey study found residues of toxaphene exceeding regulatory limits in only 1% of the 14,492 food samples. Toxaphene was reported to be among the most frequently occurring residues found in total dietary foods for the period 1982-84. It was found 48 times based on two food consumption surveys, a level higher than the frequency of DDT, DCPA, pentachloroaniline, and methoxychlor. Toxaphene has been detected in two large, pooled samples of human milk collected from mothers living in Uppsala and Stockholm at a concentration of 0.1 mg/kg of milk fat. Accumulation of toxaphene occurs in water in areas where the insecticide is in use, and it may be quite persistent. In some Canadian lakes it was found in toxic concentrations up to five yr after fish have been killed. Several studies have documented the presence of toxaphene in rain water, e.g. 9 ng/L in rain samples from Lake Michigan. It is now clear that toxaphene is a global pollutant like DDT, PCBs, and other organochlorines. Toxaphene is persistent in soils and lake sediments and has been found in fish, in the ringed seal, in rain water, and in human milk.(ABSTRACT TRUNCATED AT 400 WORDS)
毒杀芬的化学性质现已研究得较为透彻;已分离并鉴定出20种异构体。其余主要成分的分子量和分子式也已明确。目前认为,从细菌到灵长类动物等所有生物体内,毒杀芬的主要代谢降解机制是还原脱氯、还原脱氯化氢,在某些情况下还包括氧化脱氯,以产生羟基衍生物、酸或酮。早期有关毒杀芬可生物降解的报道发表于先进分析方法出现之前,而如今借助这些方法能够检测出十亿分比水平的毒杀芬。尽管1982年已禁止使用毒杀芬,但最近在整个生物圈以及人乳中都发现了其残留。这种全球持久性与以往认为毒杀芬易于生物降解的观点相悖。在过去十年里,检测技术在选择性、准确性和灵敏度方面取得了进展,因此已广泛记录了毒杀芬在整个生物圈中的存在情况。通过使用气相色谱/质谱联用仪(GC/MS)和电子捕获气相色谱仪,现在能够检测出十亿分比水平的毒杀芬,从而更一致、准确地评估该化合物在生物体以及土壤、水和地下水中的存在情况。已在人类、鱼类和野生动物、土壤、水、地下水以及食物中检测到毒杀芬残留。美国食品药品监督管理局(FDA)的一项食品调查研究发现,在14492份食品样本中,只有1%的样本中毒杀芬残留量超过监管限值。据报道,在1982 - 1984年期间,毒杀芬是总膳食食品中最常出现的残留物质之一。根据两项食品消费调查,共发现毒杀芬残留48次,这一频率高于滴滴涕、敌草索、五氯苯胺和甲氧滴滴涕。在从居住于乌普萨拉和斯德哥尔摩的母亲那里采集的两份大型母乳混合样本中,检测到毒杀芬的浓度为每千克乳脂0.1毫克。在使用该杀虫剂的地区,毒杀芬会在水中蓄积,并且可能具有相当的持久性。在加拿大的一些湖泊中,即使鱼类死亡五年后仍能检测到有毒浓度的毒杀芬。多项研究记录了雨水中毒杀芬的存在情况,例如密歇根湖雨水样本中的浓度为9纳克/升。现在很清楚,毒杀芬是一种像滴滴涕、多氯联苯和其他有机氯一样的全球污染物。毒杀芬在土壤和湖泊沉积物中具有持久性,并且已在鱼类、环斑海豹、雨水中以及人乳中被发现。(摘要截选至400字)