首页> 外文会议>International Conference on Copper 2003-Cobre 2003 v.2; 20031130-20031203; Santiago; CL >Influences of water chemistry on bioavailability and toxicity of copper to fresh water algae: an implication for the biotic ligand model (BLM)
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Influences of water chemistry on bioavailability and toxicity of copper to fresh water algae: an implication for the biotic ligand model (BLM)

机译:水化学对铜的生物利用度和铜对淡水藻类的毒性的影响:对生物配体模型(BLM)的影响

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The Biotic Ligand Model (BLM) has been previously developed to explain and predict the effects of water chemistry on the toxicity of copper to rainbow trout, fathead minnow and D. magna. In this paper, we describe the development and application of a BLM for copper to freshwater alga. The variations in Cu toxicity to alga over a range of EDTA and the site-specific variables in DOC, alkalinity and chloride were examined. Higher content of variables in EDTA, DOC, alkalinity and chloride linearly increased the 96-h EC50 (as the total Cu), supporting the concept of complexes of these ligands with Cu to reduce the chance of Cu adsorbed on the active sites at the organism-water interface. Based on the BLM concept, we developed a methodology to estimate stability constants and complexation capacity (or BL, which equals to concentration of binding sites on the single cell) for the Cu to bind biotic ligand on the basis of toxicity data. Following values were obtained: log K_(BL)= 5.8, and CCBL=5.74x10~(-8) μmol·cell~(-1). Further, we determined that the critical accumulation of Cu EC50 (or LA50) is 2.5x10~(-8) μmol·cell~(-1) corresponding to the dissolved Cu EC50, and the average 43% of biotic ligand sites need to be occupied by Cu to induce a 50% acute effect for alga after 96-h exposure. Using the estimated constants, we examine the key assumption that underlies the BLM, whose toxicity can be defined as accumulation of copper at the physiological activity sites (or biotic ligand) on the alga cell membrane at or above a critical threshold concentration. The initial BLM was developed that can predict acute Cu toxicity to alga as a function of water characteristics. After validation with reconstituted and natural waters, the developed model will support efforts to predict Cu EC50s for use in WER determinations. The presented methodology can easily be applied for BLM development for prediction of Cu toxicity to other organisms.
机译:先前已经开发了生物配体模型(BLM)来解释和预测水化学作用对铜对虹鳟鱼,黑头fat鱼和D. magna毒性的影响。在本文中,我们描述了用于淡水藻类的铜BLM的开发和应用。研究了EDTA范围内Cu对藻类的毒性变化以及DOC,碱度和氯化物中的特定位置变量。 EDTA,DOC,碱度和氯化物中变量的含量较高,线性增加了96小时EC50(以总Cu计),支持了这些配体与Cu的络合物概念,以减少Cu吸附在生物体活性位点上的机会-水界面。基于BLM概念,我们开发了一种方法,用于根据毒性数据估算铜结合生物配体的稳定性常数和络合能力(或BL,等于单个细胞上结合位点的浓度)。得到以下值:log K_(BL)= 5.8,CCBL = 5.74×10 8-(-8)μmol·cell 1-(-1)。此外,我们确定Cu EC50(或LA50)的临界累积量为2.5x10〜(-8)μmol·cell〜(-1),对应于溶解的Cu EC50,平均43%的生物配体位点需要暴露96 h后被Cu吸收,对藻类产生50%的急性影响。使用估计的常数,我们检查了BLM的关键假设,BLM的毒性可定义为在临界阈值浓度或以上时,藻类细胞膜上生理活性部位(或生物配体)处的铜累积。最初的BLM可以预测铜对藻类的急性毒性与水特性的关系。在用复原水和天然水进行验证后,开发的模型将支持预测可用于WER测定的Cu EC50的努力。所提出的方法可以很容易地应用于BLM的发展,以预测Cu对其他生物的毒性。

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