James M O
Environ Health Perspect. 1987 Apr;71:97-103. doi: 10.1289/ehp.877197.
Aquatic organisms can take up organic pollutants from their environment and subsequently excrete the pollutant or its biotransformation products (metabolites). Phase II (conjugation) biotransformation products are almost always less toxic than the unmetabolized organic pollutant. For many organic pollutants, the extent to which conjugates are formed is extremely important in determining the rate of excretion of the pollutant. This is because most conjugates (glycosides, sulfates, amino acid conjugates, mercapturic acids) are organic anions which are readily water-soluble and are rapidly excreted by fish (and probably higher invertebrates) by a combination of glomerular filtration and tubular transport. In this paper, each major conjugation pathway is discussed with respect to what is known about its occurrence in fish and aquatic invertebrates, both from in vivo and in vitro data. Although limited data are available, this paper also considers what is known about how each conjugation reaction affects the toxicity and potential for renal and biliary excretion of organic xenobiotic substrates.
水生生物能够从其生存环境中摄取有机污染物,随后排出污染物或其生物转化产物(代谢物)。第二阶段(结合)生物转化产物的毒性几乎总是低于未代谢的有机污染物。对于许多有机污染物而言,结合物的形成程度在决定污染物的排泄速率方面极为重要。这是因为大多数结合物(糖苷、硫酸盐、氨基酸结合物、硫醚氨酸)都是有机阴离子,它们极易溶于水,并通过肾小球滤过和肾小管转运的组合,被鱼类(可能还有高等无脊椎动物)迅速排出。在本文中,将根据从体内和体外数据中了解到的情况,讨论鱼类和水生无脊椎动物中每种主要结合途径的发生情况。尽管可用数据有限,但本文还考虑了关于每种结合反应如何影响有机外源性底物的毒性以及肾脏和胆汁排泄潜力的已知信息。