Department of Civil and Environmental Engineering, Manhattan College, Riverdale, New York, USA.
Environ Toxicol Chem. 2011 Jun;30(6):1278-87. doi: 10.1002/etc.518. Epub 2011 Apr 7.
The tableau input coupled kinetic equilibrium transport-unit world model (TICKET-UWM) has been developed as a screening model for assessing potential environmental risks associated with the release of metals into lakes. The model is based on a fully implicit, one-step solution algorithm that allows for simultaneous consideration of dissolved and particulate phase transport; metal complexation to organic matter and inorganic ligands; precipitation of metal hydroxides, carbonates, and sulfides; competitive interactions of metals and major cations with biotic ligands; a simplified description of biogeochemical cycling of organic carbon and sulfur; and dissolution kinetics for metal powders, massives, and other solid forms. Application of TICKET-UWM to a generalized lake in the Sudbury area of the Canadian Shield is presented to demonstrate the overall cycling of metals in lakes and the nonlinear effects of chemical speciation on metal responses. In addition, the model is used to calculate critical loads for metals, with acute toxicity of Daphnia magna as the final endpoint. Model results show that the critical loads for Cu, Ni, Pb, and Zn varied from 2.5 to 39.0 g metal/m(2) -year and were found to be one or more orders of magnitude higher than comparable loads for pesticides (lindane, 4,4'-DDT) and several polyaromatic hydrocarbon (PAH) compounds. In sensitivity calculations, critical metal-loading rates were found to vary significantly as a function of the hydraulic detention time, water hardness, and metal dissolution kinetic rates.
表输入耦合动力平衡传输单元世界模型(TICKET-UWM)已经被开发为一种筛选模型,用于评估金属释放到湖泊中与潜在环境风险相关的问题。该模型基于一个完全隐式的单步求解算法,允许同时考虑溶解相和颗粒相的传输;金属与有机物和无机配体的络合;金属氢氧化物、碳酸盐和硫化物的沉淀;金属和主要阳离子与生物配体的竞争作用;简化的有机碳和硫的生物地球化学循环描述;以及金属粉末、块状物和其他固体形式的溶解动力学。本文应用 TICKET-UWM 对加拿大盾地区 Sudbury 地区的一个典型湖泊进行了研究,以展示湖泊中金属的整体循环以及化学形态对金属响应的非线性影响。此外,该模型还用于计算金属的临界负荷,以大型溞(Daphnia magna)的急性毒性作为最终终点。模型结果表明,Cu、Ni、Pb 和 Zn 的临界负荷在 2.5 到 39.0 g 金属/m(2) -年之间变化,发现其比农药(林丹、4,4'-DDT)和几种多环芳烃(PAH)化合物的可比负荷高出一个或多个数量级。在敏感性计算中,发现临界金属负荷率随水力停留时间、水硬度和金属溶解动力学速率的变化而显著变化。