Woodfine D G, Seth R, Mackay D, Havas M
Environmental and Resource Studies, Trent University, Peterborough, Ont., Canada.
Chemosphere. 2000 Nov;41(9):1377-88. doi: 10.1016/s0045-6535(00)00006-0.
The changes in metal concentration following significant reductions in atmospheric metal loading of two nickel and copper contaminated lakes in Coniston Valley of the Sudbury Basin of Ontario, Canada were simulated by using steady-state and dynamic versions of a modified Quantitative Water Air Sediment Interaction (QWASI) Model. Metal partitioning and precipitation processes were quantified with the aid of US EPA's MINTEQA2 Model. The dynamic model successfully described the recovery of the two lakes and identified key input, loss and partitioning processes. A useful modelling strategy is to develop one or more steady-state models that give an approximate representation of conditions at defined times, then extend this to a dynamic version which can take into account the differing rates of response of components of the system. This modelling strategy can be used for designing and assessing remediation programs for metal contaminated lakes and watersheds.
通过使用改进的定量水-空气-沉积物相互作用(QWASI)模型的稳态和动态版本,模拟了加拿大安大略省萨德伯里盆地康尼斯顿山谷中两个镍和铜污染湖泊在大气金属负荷显著降低后的金属浓度变化。借助美国环境保护局的MINTEQA2模型对金属分配和沉淀过程进行了量化。动态模型成功地描述了这两个湖泊的恢复情况,并确定了关键的输入、损失和分配过程。一种有用的建模策略是开发一个或多个稳态模型,这些模型能够近似表示特定时间的状况,然后将其扩展为动态版本,该动态版本可以考虑系统各组成部分不同的响应速率。这种建模策略可用于设计和评估金属污染湖泊和流域的修复方案。