School of Environmental Sciences, University of Guelph, Guelph, Ontario, Canada.
Environ Toxicol Chem. 2013 Apr;32(4):810-21. doi: 10.1002/etc.2116. Epub 2013 Feb 19.
The effect of major cation activity (Ca(2+) , Mg(2+) , Na(+) , K(+) ) on Ni toxicity, with dose expressed as exposure (total dissolved Ni concentration NiTot ) or free Ni ion activity (in solution Ni(2+) ), or as tissue residue (Ni concentration in plant tissue NiTiss ) to the aquatic plant Lemna minor L. was examined. In addition, Ni accumulation kinetics was explored to provide mechanistic insight into current approaches of toxicity modeling, such as the tissue residue approach and the biotic ligand model (BLM), and the implications for plant Ni risk assessment. Major cations did not inhibit Ni accumulation via competitive inhibition as expected by the BLM framework. For example, Ca(2+) and Mg(2+) (sulfate as counter-anion) had an anticompetitive effect on Ni accumulation, suggesting that Ca or Mg forms a ternary complex with Ni-biotic ligand. The counter-anion of the added Ca (sulfate, chloride, or nitrate) affected plant response (percentage of root growth inhibition) to Ni. Generally, sulfate and chloride influenced plant response while nitrate did not, even when compared within the same range of Ca(2+) , which suggests that the anion dominated the observed plant response. Overall, although an effect of major cations on Ni toxicity to L. minor L. was observed at a physiological level, Ni(2+) or NiTot alone modeled plant response, generally within a span of twofold, over a wide range of water chemistry. Thus, consideration of major cation competition for improving Ni toxicity predictions in risk assessment for aquatic plants may not be necessary.
考察了主要阳离子活性(Ca(2+)、Mg(2+)、Na(+)、K(+))对水生植物浮萍(Lemna minor L.)的镍毒性的影响,剂量表示为暴露(总溶解镍浓度 NiTot)或游离镍离子活性(溶液中 Ni(2+)),或作为组织残留(植物组织中的镍浓度 NiTiss)。此外,还探讨了镍积累动力学,为当前毒性建模方法(如组织残留方法和生物配体模型(BLM))提供了机制见解,并探讨了其对植物镍风险评估的影响。主要阳离子并未通过 BLM 框架所预期的竞争抑制来抑制镍积累。例如,Ca(2+)和 Mg(2+)(硫酸盐作为抗衡阴离子)对镍积累具有拮抗作用,表明 Ca 或 Mg 与 Ni-生物配体形成三元配合物。添加的 Ca 的抗衡阴离子(硫酸盐、氯化物或硝酸盐)影响植物对 Ni 的响应(根生长抑制的百分比)。通常,硫酸盐和氯化物影响植物的响应,而硝酸盐则没有,即使在相同的 Ca(2+)范围内进行比较也是如此,这表明阴离子主导了观察到的植物响应。总体而言,尽管在生理水平上观察到主要阳离子对浮萍的镍毒性有影响,但 Ni(2+)或 NiTot 单独模拟了植物的响应,通常在广泛的水化学范围内,跨度为两倍。因此,在水生植物的风险评估中,考虑主要阳离子竞争以提高镍毒性预测的必要性可能不大。