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卤代乙腈:代谢与毒性

Haloacetonitriles: metabolism and toxicity.

作者信息

Lipscomb John C, El-Demerdash Ebtehal, Ahmed Ahmed E

机构信息

Environmental Protection Agency, National Center for Environmental Assessment, Cincinnati, Ohio 45268, USA.

出版信息

Rev Environ Contam Toxicol. 2009;198:169-200. doi: 10.1007/978-0-387-09647-6_5.

Abstract

The haloacetonitriles (HANs) exist in drinking water exclusively as byproducts of disinfection. HANs are found in drinking water more often, and in higher concentrations, when surface water is treated by chloramination. Human exposure occurs through consumption of finished drinking water; oral and dermal contact also occurs, and results from showering, swimming and other activities. HANs are reactive and are toxic to gastrointestinal tissues following oral administration. Such toxicity is characterized by GSH depletion, increased lipid peroxidation, and covalent binding of HAN-associated radioactivity to gut tissues. The presence of GSH in cells is an important protective mechanism against HAN toxicity; depletion of cellular GSH results in increased toxicity. Some studies have demonstrated an apparently synergistic effect between ROS and HAN administration, that may help explain effects observed in GI tissues. ROS are produced in gut tissues, and in vitro evidence indicates that ROS may contribute to the degradation and formation of reactive intermediates from HANs. The rationale for ROS involvement may involve HAN-induced depletion of GSH and the role of GSH in scavenging ROS. In addition to effects on GI tissues, studies show that HAN-derived radiolabel is found covalently bound to proteins and DNA in several organs and tissues. The addition of antioxidants to biologic systems protects against HAN-induced DNA damage. The protection offered by antioxidants supports the role of oxidative stress and the potential for a threshold in han-induced toxicity. However, additional data are needed to substantiate evidence for such a threshold. HANs are readily absorbed from the GI tract and are extensively metabolized. Elimination occurs primarily in urine, as unconjugated one-carbon metabolites. Evidence supports the involvement of mixed function oxidases, the cytochrome P450 enzyme family and GST, in HAN metabolism. Metabolism represents either a detoxification or bioactivation process, depending on the particular HAN and the enzyme involved. HANs can inhibit CYP2E1-mediated metabolism, an effect which may be dependent on a covalent interaction with the enzyme. In addition, HAN compounds inhibit GST-mediated conjugation, but this effect is reversible upon dialysis, indicating that the interaction does not represent covalent binding. No subchronic studies of HAN toxicity are available in the literature. However, studies show that HANs produce developmental toxicity in experimental animals. The nature of developmental toxicity is affected by the type of administration vehicle, which renders interpretation of results more difficult. Skin tumors have been found following dermal application of HANs, but oral studies for carcinogenicity are negative. Pulmonary adenomas were increased following oral administration of HANs, but the A/J strain of mice employed has a characteristically high background rate of such tumors. HANs interact with DNA to produce unscheduled DNA repair, SCE and reverse mutations in Salmonella. HANs did not induce micronuclei or cause alterations in sperm head morphology in mice, but did induce micronuclei in newts. Thus, there is concern for the potential carcinogenicity of HANs. It would be valuable to delineate any relationship between the apparent threshold for micronuclei formation in newts and the potential mechanism of toxicity involving HAN-induced oxidative stress. Dose-response studies in rodents may provide useful information on toxicity mechanisms and dose selection for longer term toxicity studies. Additional studies are warranted before drawing firm conclusions on the hazards of HAN exposure. Moreover, additional studies on HAN-DNA and HAN-protein interaction mechanisms, are needed. Such studies can better characterize the role of metabolism in toxicity of individual HANs, and delineate the role of oxidative stress, both of which enhance the capacity to predict risk. Most needed, now, are new subchronic (and chronic) toxicity studies; the results of such well-planned, controlled, conducted, interpreted and published investigations would be valuable in establishing margins of safety for HANs in human health risk assessment.

摘要

卤代乙腈(HANs)仅作为消毒副产物存在于饮用水中。当采用氯胺消毒处理地表水时,饮用水中更常发现HANs,且浓度更高。人体通过饮用成品饮用水接触HANs;口腔和皮肤接触也会发生,例如淋浴、游泳及其他活动。HANs具有反应活性,口服后对胃肠道组织有毒性。这种毒性表现为谷胱甘肽(GSH)耗竭、脂质过氧化增加以及HAN相关放射性与肠道组织的共价结合。细胞内GSH的存在是抵御HAN毒性的重要保护机制;细胞内GSH耗竭会导致毒性增加。一些研究表明活性氧(ROS)与HAN给药之间存在明显的协同效应,这可能有助于解释在胃肠道组织中观察到的效应。ROS在肠道组织中产生,体外证据表明ROS可能有助于HANs的降解及活性中间体的形成。ROS参与其中的原理可能涉及HAN诱导的GSH耗竭以及GSH在清除ROS中的作用。除了对胃肠道组织的影响外,研究表明HAN衍生的放射性标记物共价结合在多个器官和组织的蛋白质和DNA上。向生物系统中添加抗氧化剂可防止HAN诱导的DNA损伤。抗氧化剂提供的保护支持了氧化应激的作用以及HAN诱导毒性中存在阈值的可能性。然而,需要更多数据来证实这种阈值的证据。HANs易于从胃肠道吸收并广泛代谢。主要通过尿液以未结合的一碳代谢物形式排出。有证据支持混合功能氧化酶、细胞色素P450酶家族和谷胱甘肽S-转移酶(GST)参与HAN代谢。代谢根据特定的HAN和所涉及的酶代表解毒或生物活化过程。HANs可抑制CYP2E1介导的代谢,这种效应可能取决于与该酶的共价相互作用。此外,HAN化合物抑制GST介导的结合,但透析后这种效应是可逆的,表明这种相互作用不代表共价结合。文献中没有关于HAN毒性的亚慢性研究。然而,研究表明HANs在实验动物中产生发育毒性。发育毒性的性质受给药载体类型的影响,这使得结果的解释更加困难。经皮肤涂抹HANs后发现有皮肤肿瘤,但口服致癌性研究结果为阴性。口服HANs后肺腺瘤增加,但所使用的A/J品系小鼠此类肿瘤的背景发生率通常较高。HANs与DNA相互作用可导致DNA非程序性修复、姐妹染色单体交换(SCE)以及沙门氏菌中的回复突变。HANs未在小鼠中诱导微核或引起精子头部形态改变,但在蝾螈中诱导了微核。因此,人们担心HANs的潜在致癌性。阐明蝾螈中微核形成的明显阈值与涉及HAN诱导氧化应激的潜在毒性机制之间的任何关系将是有价值的。啮齿动物的剂量反应研究可能为毒性机制和长期毒性研究的剂量选择提供有用信息。在就HAN暴露的危害得出确凿结论之前,有必要进行更多研究。此外,还需要对HAN-DNA和HAN-蛋白质相互作用机制进行更多研究。此类研究可以更好地描述代谢在个体HANs毒性中的作用,并阐明氧化应激的作用,这两者都能增强预测风险的能力。目前最需要的是新的亚慢性(和慢性)毒性研究;此类精心规划、控制、实施、解释和发表的研究结果对于确定HANs在人类健康风险评估中的安全边际将是有价值的。

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