Liess Matthias, Pieters Barry Johan, Duquesne Sabine
UFZ-Centre for Environmental Research Umweltforschungszentrum Leipzig-Halle GmbH, Permoserstrasse 15, D-04318 Leipzig, Germany.
Environ Toxicol Chem. 2006 May;25(5):1326-31. doi: 10.1897/05-466r.1.
Little is known about the effect of pulse exposure to toxicants on populations when density regulation is present. Yet, for a more realistic risk assessment, it is necessary to include effect and recovery at the population level. Here, we investigate the long-term and delayed effects as well as the subsequent recovery of populations of Daphnia magna. A 24-h pulse of the pyrethroid fenvalerate reduced the abundance at a concentration of 1.0 microg/L and higher. However, abundance recovered and reached control levels after one to two generation times (GTs) following reproduction of surviving individuals (GT = 8 d, from birth until first reproduction). At high concentrations above the acute median lethal concentration (3.2 micorg/L), abundance initially decreased even more strongly but was then elevated compared to control values for an extended period of time. Population structure (size distribution) was affected at lower concentrations than abundance (> 0.8 microg/L). In addition, the alteration of population structure lasted for a long time, so that control levels were approached only after approximately six or seven GTs. Our results show that pulse exposure to toxicants may lead to a long-term alteration of population structure even at sublethal concentrations. Possible mechanisms that sustain the effects of toxicants may be delayed life-history effects on the individual level and elevated competition because of altered population structure on the population level.
对于存在密度调节时毒物脉冲暴露对种群的影响,人们了解甚少。然而,为了进行更现实的风险评估,有必要纳入种群水平的效应和恢复情况。在此,我们研究大型溞种群的长期和延迟效应以及随后的恢复情况。拟除虫菊酯氰戊菊酯24小时的脉冲暴露在浓度为1.0微克/升及更高时降低了种群数量。然而,在存活个体繁殖后的一到两个世代时间(世代时间 = 8天,从出生到首次繁殖)后,种群数量恢复并达到对照水平。在高于急性半数致死浓度(3.2微克/升)的高浓度下,种群数量最初下降得更为强烈,但随后在较长一段时间内高于对照值。种群结构(大小分布)在比种群数量更低的浓度(> 0.8微克/升)下就受到影响。此外,种群结构的改变持续了很长时间,以至于仅在大约六到七个世代时间后才接近对照水平。我们的结果表明,即使在亚致死浓度下,毒物脉冲暴露也可能导致种群结构的长期改变。维持毒物效应的可能机制可能是个体水平上延迟的生活史效应以及种群水平上因种群结构改变而加剧的竞争。