Edginton Andrea N, Rouleau Claude, Stephenson Gerald R, Boermans Herman J
Department of Environmental Biology, University of Guelph, Guelph, Ontario, N1G 2W1, Canada.
Arch Environ Contam Toxicol. 2007 Jan;52(1):113-20. doi: 10.1007/s00244-005-0215-4. Epub 2006 Oct 9.
The role of the jelly coat in providing a protective barrier to chemical absorption was studied using the embryos of the amphibian, Xenopus laevis. Embryos with or without a jelly coat were water exposed to the butoxyethyl ester of 2,4-dichlorophenoxyacetic acid (2,4-D BEE) and the rates of uptake, metabolism, distribution, and excretion were determined. The water uptake clearance rates were slower for embryos with a jelly coat (1.5-4.5 ml(water).g (embryo) (-1).h(-1) or 0.040-0.022 ml(water).h(-1) per embryo) in comparison to dejellied embryos (14-21 ml(water).g (embryo) (-1).h(-1) 0.0066-0.021 ml(water).h(-1) per embryo). This accounted for the much lower residues in embryos with a jelly coat than in dejellied embryos during 8 h of exposure. Despite quantitative differences in uptake, once 2,4-D BEE had entered the embryos, metabolism and distribution were similar between the two test groups. 2,4-D BEE was metabolized to 2,4-dichlorophenoxyacetic acid (2,4-D) with half-lives ranging from 35 to 42 minutes. The radioactive residues, as determined by whole body autoradiography, appeared throughout the embryo with a slight accumulation in the blastocoel. Furthermore, 35% of the radioactive residues were located in the jelly coat and 65% in the developing embryo. Based on a slower 2,4-D elimination in embryos with a jelly coat, the diffusive properties that decreased 2,4-D BEE uptake appeared to similarly decrease elimination of its metabolite. The common practice of removing jelly coats prior to embryonic amphibian toxicity studies, as in the widely used Frog Embryo Teratogenesis Assay-Xenopus (FETAX), is discouraged based on the kinetic differences observed in this study.
利用非洲爪蟾(Xenopus laevis)的胚胎研究了卵胶膜在提供化学物质吸收保护屏障方面的作用。将有或没有卵胶膜的胚胎暴露于2,4-二氯苯氧乙酸丁氧基乙酯(2,4-D BEE)的水中,并测定其摄取、代谢、分布和排泄速率。与去卵胶膜的胚胎相比,有卵胶膜的胚胎的水摄取清除率较慢(1.5 - 4.5 ml(水)·g(胚胎)⁻¹·h⁻¹或每个胚胎0.040 - 0.022 ml(水)·h⁻¹)(去卵胶膜的胚胎为14 - 21 ml(水)·g(胚胎)⁻¹·h⁻¹或每个胚胎0.0066 - 0.021 ml(水)·h⁻¹)。这解释了在暴露8小时期间,有卵胶膜的胚胎中的残留物比去卵胶膜的胚胎中的残留物低得多的原因。尽管摄取量存在定量差异,但一旦2,4-D BEE进入胚胎,两个测试组之间的代谢和分布是相似的。2,4-D BEE代谢为2,4-二氯苯氧乙酸(2,4-D),半衰期为35至42分钟。通过全身放射自显影测定,放射性残留物出现在整个胚胎中,在囊胚腔中有轻微积累。此外,35%的放射性残留物位于卵胶膜中,65%位于发育中的胚胎中。基于有卵胶膜的胚胎中2,4-D消除较慢,降低2,4-D BEE摄取的扩散特性似乎同样降低了其代谢物的消除。基于本研究中观察到的动力学差异,不鼓励在两栖动物胚胎毒性研究之前去除卵胶膜的常见做法,如在广泛使用的爪蟾胚胎致畸试验(FETAX)中那样。