Lemly A D
Ecotoxicol Environ Saf. 1985 Dec;10(3):314-38. doi: 10.1016/0147-6513(85)90079-x.
A study was conducted to document patterns of accumulation and toxicity of selenium to organisms in a power plant cooling reservoir in North Carolina. Selenium entered the reservoir by way of effluent from the coal ash disposal basin, which contained 100-200 micrograms Se/liter. Concentrations of selenium in the lake water averaged 10 micrograms/liter, but were accumulated from 519 times (periphyton) to 3975 times (visceral tissue, largemouth bass) in the biota. The pattern and degree of accumulation was essentially complete within 2 years after the initial operation of the power plant, and persisted throughout the remainder of the study: fishes greater than insects greater than annelids greater than molluscs greater than crustaceans greater than plankton greater than periphyton. The plantonic and detrital food pathways exposed fishes to potential dietary concentrations of selenium that were some 770 and 519-1395 times the waterborne exposure, respectively. Of the 20 species of fish originally present in the reservoir, 16 were entirely eliminated, 2 were rendered sterile but persisted as adults, 1 was eliminated but managed to recolonize from a relatively uncontaminated headwater area as sterile adults, and 1 was unaffected. Two nonnative fish species were accidentally introduced and established reproducing populations. Abundance and diversity of biota other than fishes was not affected. Relative to control habitats, the contaminated reservoir had concentrations of waterborne selenium that were 20-30 times background levels; the flora and fauna contained about 10-15 times background. The results show that selenium can accumulate and be biologically magnified to toxic levels in a reservoir even though waterborne concentrations are in the low microgram per liter range. This study also provides data which indicate that current toxicological information is neither accurate when used to predict the relative sensitivity of individual fish species to selenium, nor is it sufficient to predict community responses in a natural setting. It is very likely that long-term elevation of waterborne selenium to 8-10 micrograms/liter in warm-water lakes and reservoirs would result in biotic responses similar to those documented in this report.
开展了一项研究,以记录北卡罗来纳州一座发电厂冷却蓄水池中硒对生物的积累模式和毒性。硒通过煤灰处理池的废水进入蓄水池,该废水中硒的含量为100 - 200微克/升。湖水中硒的浓度平均为10微克/升,但在生物群中积累了519倍(附生植物)至3975倍(内脏组织,大口黑鲈)。在发电厂首次运行后的2年内,积累模式和程度基本完成,并在研究的剩余时间内持续存在:鱼类 > 昆虫 > 环节动物 > 软体动物 > 甲壳类动物 > 浮游生物 > 附生植物。浮游和碎屑食物途径使鱼类接触到的潜在膳食硒浓度分别约为水体暴露浓度的770倍和519 - 1395倍。蓄水池中原本存在的20种鱼类中,16种完全消失,2种不育但成年后仍存活,1种消失但作为不育成年鱼从相对未受污染的上游区域重新定殖,1种未受影响。两种非本地鱼类意外引入并建立了繁殖种群。鱼类以外的生物群的丰度和多样性未受影响。相对于对照栖息地,受污染的蓄水池中水体硒浓度是背景水平的20 - 30倍;动植物体内的硒含量约为背景的10 - 15倍。结果表明,即使水体硒浓度处于每升几微克的低水平,硒仍可在蓄水池中积累并通过生物放大作用达到有毒水平。这项研究还提供了数据,表明当前的毒理学信息在用于预测单个鱼类物种对硒的相对敏感性时既不准确,也不足以预测自然环境中的群落反应。在温水湖泊和蓄水池中,水体硒长期升高至8 - 10微克/升很可能会导致与本报告中记录的类似生物反应。