Toxicology Centre, University of Saskatchewan, 44 Campus Drive, Saskatoon, Saskatchewan S7 N 5B3, Canada.
Arch Environ Contam Toxicol. 2009 Oct;57(3):531-9. doi: 10.1007/s00244-009-9283-1. Epub 2009 Jan 16.
Limited data are available on the effects of uranium (U) exposures on benthic macroinvertebrates, something that would be needed before national or provincial water quality guidelines could be developed. The goal of this study was to evaluate chronic U toxicity and accumulation in the aquatic invertebrate Chironomus tentans. Test organisms were exposed to three aqueous U concentrations (40, 200, and 1,000 microg/L) and an untreated control. Larval growth, adult emergence, and U tissue concentrations at different life stages were evaluated. The measured no-observed-effect concentration (NOEC) and lowest-observed-effect concentration (LOEC) for growth of C. tentans larvae after 10 days of U exposure were 39 and 157 microg/L, respectively. At U concentrations >157 ug/L, there was reduced larval growth of 30% to 40%, which corresponded to reduced adult emergence of 40% to 60%. Despite significant delays in time to adult emergence, there were no significant effects on reproductive output of successfully emerged adults. The F(1) generation C. tentans larvae that were never directly exposed to U, but originated from adult males and females exposed to U during their immature life stages, displayed a significant decrease in 10-day growth that was similar to that observed for the F(0)-exposed larvae. This suggests that the environment of the parental generation can significantly influence the development of the next generation through environmentally induced parental effects. Uranium accumulated in C. tentans immature stages was partially excreted during molting and metamorphosis to the adult stage. However, the elimination of U was not complete and some was still measured in adult midges. Consequently, a minor transfer of U from the aquatic to the terrestrial environment could be expected to occur.
关于铀(U)暴露对底栖大型无脊椎动物的影响的数据有限,在制定国家或省级水质指南之前,这是必要的。本研究的目的是评估水生无脊椎动物摇蚊在慢性 U 毒性和积累方面的情况。测试生物暴露于三种水溶液 U 浓度(40、200 和 1000μg/L)和未处理的对照中。评估了幼虫生长、成虫出现以及不同生命阶段的 U 组织浓度。在 U 暴露 10 天后,测量到对摇蚊幼虫生长的无观察效应浓度(NOEC)和最低观察效应浓度(LOEC)分别为 39 和 157μg/L。在 U 浓度>157μg/L 时,幼虫生长减少 30%至 40%,这对应于成虫出现减少 40%至 60%。尽管成虫出现的时间明显延迟,但对成功出现的成虫的生殖输出没有显著影响。从未直接暴露于 U 的 F1 代摇蚊幼虫,但源自在其不成熟生命阶段暴露于 U 的成年雄性和雌性,显示出 10 天生长的显著下降,与 F0 暴露幼虫观察到的相似。这表明,亲代的环境可以通过环境诱导的亲代效应显著影响下一代的发育。在向成虫阶段变态期间,U 积累在摇蚊不成熟阶段中部分被排泄。然而,U 的消除并不完全,一些仍在成年摇蚊中测量到。因此,预计 U 会从水生环境少量转移到陆地环境中。