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CAN THE UNIT WORLD MODEL CONCEPT BE APPLIED TO HAZARD ASSESSMENT OF BOTH ORGANIC CHEMICALS AND METAL IONS?

机译:可以将UNIT WORLD MODULE概念应用于有机化学物质和金属离子的危险性评估吗?

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A unit world model that has the potential to be used for the hazard assessment of both metal ions and organic chemicals is described and discussed, with an emphasis on the problems that arise when treating metal ions. It is based on the steady-state equilibrium criterion model that is designed to simulate the fate of organic chemicals in a 100,000-km2 region and comprises four well-mixed compartments: Air, water, soil, and sediment. To be applicable to metal ions, modifications are required. The single soil and sediment layers should be replaced by two layers to accommodate aerobic and anaerobic conditions. The more complex and variable partitioning of metals resulting from dependence on pH, redox conditions, ionic oxidation state, and presence of sulfide also must be addressed, but preferably in a separate geochemical model, because these factors can result in nonlinearity. For metals, a dynamic as well as a steady-state model is desirable. It is shown that the resulting model can be applied to both organics and metals. Rather than seeking to apply the hazard criterion of persistence to metal ions, the model can be used to deduce a critical loading that results in a defined toxic end point, thus integrating the hazard criteria of persistence, toxicity, and possibly, bioaccumulation. This approach is applied illustratively to naphthalene as a typical organic substance and to four environmentally relevant metal ions. Results are discussed and recommendations made for further development. Specifically, the absence of metal degradation can result in large, steady-state quantities in soils and sediments corresponding to residence times of many centuries. Consequently, the dynamic calculations are more relevant for fate assessments of metals over a period of years, and more focus on the aquatic environment is justified.
机译:描述和讨论了一个有可能用于金属离子和有机化学物质危害评估的单位世界模型,重点是处理金属离子时出现的问题。它基于稳态平衡标准模型,该模型旨在模拟100,000平方公里区域内有机化学品的命运,并包括四个充分混合的隔室:空气,水,土壤和沉积物。为了适用于金属离子,需要进行修饰。应将单层土壤和沉积物层替换为两层,以适应有氧和厌氧条件。还必须解决由于依赖于pH值,氧化还原条件,离子氧化态和硫化物的存在而导致的金属的更复杂和可变的分配,但最好在单独的地球化学模型中进行,因为这些因素会导致非线性。对于金属,理想的是动态模型和稳态模型。结果表明,所得模型可应用于有机物和金属。可以使用该模型来推导出导致定义的毒性终点的临界载荷,而不是试图对金属离子应用持久性危险标准,从而整合持久性,毒性和可能的​​生物蓄积性危险标准。该方法示例性地应用于作为典型有机物质的萘和四种与环境有关的金属离子。讨论了结果并提出了进一步发展的建议。具体而言,不存在金属降解会导致土壤和沉积物中大量稳态状态的变化,对应多个世纪的停留时间。因此,动态计算与过去几年中金属的命运评估更加相关,并且更多地关注水生环境是合理的。

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