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The challenges of hazard identification and classification of insoluble metals and metal substances

机译:危害识别和不溶性金属物质分类的挑战

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Procedures for aquatic hazard identification of organic and inorganic substances are currently being harmonized by the OECD for the purpose of classifying market-place substances. Such a system already exists in Europe and is evolving other countries (United States and Canada). One common theme in each of these systems is the use of toxicity, persistence and bioaccumulation measurements to estimate aquatic hazard. It is recognized a within the OECD and European Union systems that special attention must be given to metal elements and sparingly soluble metal-containing compounds. This recognition is based upon a common understanding that standard hazard testing procedures designed for soluble organic chemicals do not accommodate the special characteristics of sparingly soluble metals and metal compounds (SSMMCs). Toxicity - it is recognized that the toxicity of a metal is due predominantly to the free metal ion in solution (estimated by soluble metal). Most of the toxicity data available to date have been derived using soluble metal salts. The assumption is that the dissolved metal ion is completely available. The toxicity of most dissolved metal salts to sensitive species lies in the range of 0.1 to 1000 ug/L (Table 1). In order to assess the acute aquatic toxicity of SSMMCs the rate and extent of transformation of metal to a soluble form must be measured. Transformation of insoluble metal substances to soluble forms is a function of several key factors including particle size, surface area, ionic strength, and the pH of the test solution. A standard protocol for measuring transformation is currently being developed by the OECD. Initial results obtained using the protocol under development indicate that unrealistically high concentrations of soluble metal are obtained as compared to concentrations that occur in natural environments (Table 2). The protocol at present lacks complexing ligands. Further development of this protocol is planned.
机译:经合组织目前正在通过经合组织统一市场地点物质的目前统一水生危害鉴定程序。这样的系统已经存在于欧洲,正在发展其他国家(美国和加拿大)。这些系统中的每一个中的一个常见主题是使用毒性,持久性和生物积累测量来估计水生危害。在经合组织和欧盟和欧盟系统内承认,必须特别注意金属元素和含有含金属的化合物。本识别基于常识,即用于可溶性有机化学品的标准危险测试程序不会适应污染可溶性金属和金属化合物(SSMMC)的特殊特征。毒性 - 认识到,金属的毒性主要是由于溶液中的游离金属离子(通过可溶性金属估计)。最迄今为止可用的大多数毒性数据使用可溶性金属盐来得出。假设是溶解的金属离子是完全可用的。最溶解的金属盐对敏感物种的毒性在0.1至1000ug / L的范围内(表1)。为了评估SSMMCS的急性水生毒性,必须测量金属转化为可溶性形式的速率和程度。不溶性金属物质对可溶性形式的转化是若干关键因子的函数,包括粒度,表面积,离子强度和测试溶液的pH。目前由经合组织开发了一种用于测量变换的标准方案。使用下发育的方案获得的初始结果表明,与天然环境中发生的浓度相比,获得了不切实际的高浓度的可溶性金属(表2)。目前的方案缺乏络合配体。计划进一步发展本协议。

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