Bossuyt Bart T A, Muyssen Brita T A, Janssen Colin R
Laboratory of Environmental Toxicology and Aquatic Ecology, Ghent University, B-9000 Ghent, Belgium.
Environ Toxicol Chem. 2005 Feb;24(2):470-8. doi: 10.1897/03-067r.1.
Species sensitivity distributions (SSD) were constructed using acute toxicity data of various cladoceran species collected in five different aquatic systems. The aim of this research was to study the relative acute cladoceran community sensitivity in different aquatic systems. Current risk assessment procedures are based upon hypothetical communities and do not take into account variation in species composition and tolerance between aquatic communities. Two metals, copper and zinc, were used as model toxicants. To establish comparative sensitivity, a standard medium (International Organization for Standardization [ISO]) was used. The generic SSD (log-normal distribution) based on toxicity data obtained in this standard medium for all species (collected at all sites) resulted in a hazardous concentrations that protects 95% of the species occurring in a (hypothetical) ecosystem (i.e., hazardous concentration protecting 95% of the species of the hypothetical ecosystem [HC5]) of 6.7 microg Cu L(-1) (90% confidence limits: 4.2-10.8) and 559 microg Zn L(-1) (375-843). This generic SSD was not significantly different from the site-specific SSDs (i.e., constructed with species only occurring at a specific site). Mean community sensitivity (the geometric mean of 48-h 50% effective concentration [EC50] values of species within a community) among sites varied within a factor of 2 (between 17.3 and 23.6 microg Cu L(-1) for Cu and between 973 and 1,808 microg Zn L(-1) for Zn), and HC5s varied within a factor of 4 for copper (between 4.5 and 17.3 microg Cu L(-1)) and 7 for zinc (between 194 and 1,341 microg Zn L(-1)). For copper, the HC50 of our generic SSD was significantly lower than the one based on literature toxicity data of cladoceran species (which were recalculated to the hardness of our standard medium). In contrast, no significant differences were observed between the generic SSD and the literature-based SSD for zinc. It is suggested that the community sensitivity of different cladoceran populations is similar among aquatic systems and is not dependent on the species composition.
利用在五个不同水生系统中收集的各种枝角类物种的急性毒性数据构建了物种敏感度分布(SSD)。本研究的目的是研究不同水生系统中枝角类群落相对急性敏感度。当前的风险评估程序基于假设群落,未考虑水生群落之间物种组成和耐受性的差异。使用铜和锌这两种金属作为模型毒物。为了确定比较敏感度,采用了一种标准介质(国际标准化组织[ISO])。基于在该标准介质中获得的所有物种(在所有站点收集)毒性数据的通用SSD(对数正态分布)得出,保护(假设)生态系统中95%物种的危险浓度(即保护假设生态系统中95%物种的危险浓度[HC5])为铜6.7微克/升(90%置信限:4.2 - 10.8)和锌559微克/升(375 - 843)。这种通用SSD与特定站点的SSD(即仅由特定站点出现的物种构建)没有显著差异。各站点间平均群落敏感度(群落内物种48小时50%有效浓度[EC50]值的几何平均值)相差2倍(铜为17.3至23.6微克/升,锌为973至1808微克/升),HC5s铜相差4倍(4.5至17.3微克/升),锌相差7倍(194至1341微克/升)。对于铜,我们通用SSD的HC50显著低于基于枝角类物种文献毒性数据(重新计算为我们标准介质的硬度)得出的HC50。相比之下,锌的通用SSD与基于文献的SSD之间未观察到显著差异。研究表明,不同枝角类种群在水生系统中的群落敏感度相似,且不依赖于物种组成。