首页> 外文会议>Strategies to Enhance Environmental Security in Transition Countries; NATO Security Through Science Series C: Environmental Security >25. WHICH HUMAN AND TERRESTRIAL ECOLOGICAL RECEPTORS ARE MOST AT RISK FROM SMELTER EMISSIONS?
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25. WHICH HUMAN AND TERRESTRIAL ECOLOGICAL RECEPTORS ARE MOST AT RISK FROM SMELTER EMISSIONS?

机译:25.哪些人类和陆地生态受体最容易受到冶炼厂排放的威胁?

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Base-metal smelters, which operated more than 100 years ago and may continue to operate, are found in many countries. These smelters have released sulfr dioxide (SO_2) and metal particulates (e.g., arsenic, cadmium, copper, nickel, lead, and zinc) into the local and regional environment. Human health risk assessments (HHRAs) and ecological risk assessments (ERAs) are required by contaminated site regulatory programs in many countries. Regional- or landscape-scale risk assessments are nearing completion for areas surrounding several of these smelters in Canada, the USA, and Europe. Valued ecosystem components (VECs) that were assessed in the terrestrial components of the ERAs are similar to those assessed in any terrestrial ERA, including plant communities, soil invertebrate communities, birds, and mammals. Results from completed ERAs clearly illustrate which VECs are most at risk. Although the emissions histories, ecosystems, metals, and VECs may be different, the conclusions are similar; plant communities are most at risk around smelters, and impacts to plant communities can have an impact on wildlife due to changes in habitat. In transition countries, such as Romania, the focus remains on human health impacts. Results from an HHRA conducted for a lead smelter in Romania are consistent with those for a lead smelter in Canada and results from smelters from other countries. Children are most at risk from ingestion of deposited dust from airborne emissions from lead smelters, but also from soil ingestion and dust inhalation. This can be monitored via a program to measure blood lead levels in young children. Various programs can be implemented to decrease exposure of children to metals around smelters. In addition, improvements in human health, plant communities (and wildlife habitats) can be made through the decrease in SO_2 and metal emissions.
机译:在许多国家/地区都有运行100多年并可能继续运行的贱金属冶炼厂。这些冶炼厂已将二氧化硫(SO_2)和金属微粒(例如砷,镉,铜,镍,铅和锌)释放到本地和区域环境中。在许多国家,受污染的场地监管计划要求进行人类健康风险评估(HHRA)和生态风险评估(ERA)。加拿大,美国和欧洲的一些冶炼厂周围地区的区域或景观风险评估已接近完成。在ERA的陆地成分中评估的有价值的生态系统成分(VEC)与在任何陆地ERA中评估的生态系统成分(VEC)相似,包括植物群落,土壤无脊椎动物群落,鸟类和哺乳动物。完整ERA的结果清楚地说明了哪些VEC风险最大。尽管排放历史,生态系统,金属和VEC可能有所不同,但结论相似。熔炉周围的植物群落受到的威胁最大,由于栖息地的变化,对植物群落的影响可能会对野生生物产生影响。在罗马尼亚等转型国家,重点仍然放在对人类健康的影响上。 HHRA在罗马尼亚的铅冶炼厂进行的结果与加拿大的铅冶炼厂的结果以及其他国家/地区的冶炼厂的结果一致。铅冶炼厂通过空气传播的污染物摄入的粉尘,以及土壤的吸收和粉尘的吸入,对儿童的危害最大。这可以通过测量幼儿血铅水平的程序进行监控。可以实施各种计划来减少儿童接触冶炼厂周围的金属。此外,可以通过减少SO_2和金属排放来改善人类健康,植物群落(和野生动植物栖息地)。

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