Santore R C, Di Toro D M, Paquin P R, Allen H E, Meyer J S
HydroQual Environmental Engineers and Scientists, Camillus, New York 13031, USA.
Environ Toxicol Chem. 2001 Oct;20(10):2397-402.
The biotic ligand model (BLM) was developed to explain and predict the effects of water chemistry on the acute toxicity of metals to aquatic organisms. The biotic ligand is defined as a specific receptor within an organism where metal complexation leads to acute toxicity. The BLM is designed to predict metal interactions at the biotic ligand within the context of aqueous metal speciation and competitive binding of protective cations such as calcium. Toxicity is defined as accumulation of metal at the biotic ligand at or above a critical threshold concentration. This modeling framework provides mechanistic explanations for the observed effects of aqueous ligands, such as natural organic matter, and water hardness on metal toxicity. In this paper, the development of a copper version of the BLM is described. The calibrated model is then used to calculate LC50 (the lethal concentration for 50% of test organisms) and is evaluated by comparison with published toxicity data sets for freshwater fish (fathead minnow, Pimephales promelas) and Daphnia.
生物配体模型(BLM)的建立是为了解释和预测水化学对金属对水生生物急性毒性的影响。生物配体被定义为生物体内的特定受体,金属络合在此处会导致急性毒性。BLM旨在预测在水合金属形态以及诸如钙等保护性阳离子的竞争性结合的背景下,生物配体处的金属相互作用。毒性被定义为金属在生物配体处积累至临界阈值浓度或高于该浓度。该建模框架为诸如天然有机物等水合配体以及水硬度对金属毒性的观测效应提供了机理解释。本文描述了BLM铜版本的开发。然后使用校准后的模型来计算LC50(50%受试生物的致死浓度),并通过与已发表的淡水鱼(黑头呆鱼,肥头鲦鱼)和水蚤毒性数据集进行比较来进行评估。