Kraak M H, Lavy D, Peeters W H, Davids C
Department of Aquatic Ecotoxicology, University of Amsterdam, The Netherlands.
Arch Environ Contam Toxicol. 1992 Oct;23(3):363-9. doi: 10.1007/BF00216246.
In order to evaluate ecological consequences of the long-term presence of metals in aquatic ecosystems, we investigated the filtration rate and survival of zebra mussels (Dreissena polymorpha) during chronic exposure to Cu and Cd. The filtration rate was measured once a week in laboratory experiments lasting 9-11 weeks. The lowest Cu concentration tested (13 micrograms/L) did not affect the filtration rate and survival of D. polymorpha, but the lowest Cd concentration (9 micrograms/L) did affect the filtration rate, but had no effect on survival. The EC50 for Cd decreased markedly from 388 micrograms/L to 27 micrograms/L when the exposure time was lengthened from 48 hours to 10 weeks. The largest decrease in EC50 for Cd was observed during the first week of exposure. In contrast, the EC50 for Cu did not decrease with increasing exposure time (chronic EC50: 43 micrograms/L). Since the chronic LC50 for Cd was 130 micrograms/L, the filtration rate appeared to be a far more sensitive endpoint for ecotoxicological laboratory experiments than mortality. D. polymorpha was capable of regulating the body concentration of the essential metal Cu at low concentrations in the water (13 micrograms/L). Cd was accumulated at every Cd concentration in the water, suggesting that Cd could not be regulated by D. polymorpha. It is concluded that the relation between short-term and long-term ecotoxicity was different for each metal and could not be predicted from the results of the short-term experiments.
为了评估金属在水生生态系统中长期存在的生态后果,我们研究了斑马贻贝(多形饰贝)在长期暴露于铜和镉环境下的滤食率和存活率。在持续9至11周的实验室实验中,每周测量一次滤食率。所测试的最低铜浓度(13微克/升)并未影响多形饰贝的滤食率和存活率,但最低镉浓度(9微克/升)确实影响了滤食率,但对存活率没有影响。当暴露时间从48小时延长至10周时,镉的半数效应浓度(EC50)从388微克/升显著降至27微克/升。镉的EC50在暴露的第一周下降幅度最大。相比之下,铜的EC50并未随暴露时间增加而降低(慢性EC50:43微克/升)。由于镉的慢性半数致死浓度(LC50)为130微克/升,对于生态毒理学实验室实验而言,滤食率似乎是比死亡率更为敏感的终点指标。多形饰贝能够在水中低浓度(13微克/升)时调节必需金属铜的体内浓度。水中的每个镉浓度下都有镉的积累,这表明多形饰贝无法对镉进行调节。得出的结论是,每种金属的短期和长期生态毒性之间的关系各不相同,无法从短期实验结果中预测。