Liao Chung-Min, Jou Li-John, Lin Chieh-Ming, Chiang Kuo-Chin, Yeh Ching-Hung, Chou Berry Yun-Hua
Department of Bioenvironmental Systems Engineering, National Taiwan University, Taipei, Taiwan, Republic of China.
Environ Toxicol. 2007 Jun;22(3):295-307. doi: 10.1002/tox.20263.
The objective of this paper is to employ biotic ligand model (BLM) to link between acute copper (Cu) toxicity and its effect on valve closure behavior of freshwater clam Corbicula fluminea in order to further support for the BLM that potentially offers a rapid and cost-effective method to conduct the acute toxicity tests for freshwater clam exposed to waterborne Cu. Reanalysis of published experimental data of C. fluminea closure daily rhythm and dose-response profiles based on the laboratory-acclimated clams showed that a BLM-based Hill model best described the free Cu(2+)-activity-valve closure response relationships. Our proposed Cu-BLM-Corbicula model shows that free ionic form of waterborne Cu binds specifically to a biotic ligand (i.e., clam gills) and impairs normal valve closure behavior, indicating that a fixed-level of metal accumulation at a biotic ligand is required to elicit specific biological effects. With derived mechanistic-based Cu-BLM-Corbicula model, we show that the site-specific EC50(t) and valve closure behavior at any integrated time can be well predicted, indicating that our model has the potential to develop a biomonitoring system as a bioassay tool to on-line measure waterborne Cu levels in aquatic systems. Our results confirm that BLM can be improved to analytically and rigorously describe the bioavailable fraction of metal causing toxicity to valve closure behavior in freshwater C. fluminea. We suggest that the Cu-BLM-Corbicula model can be used to assist in developing technically defensible site-specific water quality criteria and performing ecological risk assessment and to promote more focused and efficient uses of resources in the regulation and control of metals and the protection of the aquatic ecosystems.
本文的目的是运用生物配体模型(BLM)将急性铜(Cu)毒性与其对淡水蚬Corbicula fluminea瓣膜关闭行为的影响联系起来,以便进一步支持BLM,该模型可能提供一种快速且经济高效的方法来对暴露于水中铜的淡水蚬进行急性毒性测试。基于实验室驯化的蚬,对已发表的C. fluminea关闭日节律和剂量反应曲线的实验数据进行重新分析表明,基于BLM的希尔模型能最好地描述游离铜离子(Cu(2+))活性与瓣膜关闭反应之间的关系。我们提出的铜 - BLM - 蚬模型表明,水中铜的游离离子形式特异性地与生物配体(即蚬鳃)结合,损害正常的瓣膜关闭行为,这表明在生物配体上需要一定水平的金属积累才能引发特定的生物学效应。通过推导基于机制的铜 - BLM - 蚬模型,我们表明可以很好地预测任何积分时间的位点特异性半数效应浓度(EC50(t))和瓣膜关闭行为,这表明我们的模型有潜力开发一种生物监测系统,作为一种生物测定工具来在线测量水生系统中水中铜的水平。我们的结果证实,可以改进BLM以分析性和严格地描述导致淡水C. fluminea瓣膜关闭行为毒性的金属生物可利用部分。我们建议铜 - BLM - 蚬模型可用于协助制定技术上合理的特定地点水质标准以及进行生态风险评估,并促进在金属调控和水生生态系统保护中更有针对性和高效地利用资源。