芜湖市郊土壤污染对土壤动物群落结构的影响

研究表明，芜湖市郊农田土壤动物群落的组成与数量随污染程度的加重而减少，土壤动物密度也呈同样的变化趋势，特别是中小型土壤动物，优势类群数量发生较大消长，常见类群和稀有类群的组成逐渐减少．多样性指数H与重金属污染程度之间关系因受到季节的影响而变得复杂：冬季和初夏污染较重样地优势类群数量减少，群落均匀性指数E增加而优势度指数C减小，多样性指数H较高；而春季处于过渡阶段，某些类群(如螨类)数量爆发，C增高，H较小．土壤动物群落密度一类群指数DG随污染加重而减小．受到重金属污染的农田土壤动物的表聚性减弱，甚至出现逆分布现象．图1表4参15     

A Geochemical Survey of Topsoil in the City of Oslo, Norway

The city of Oslo is situated centrally in the Oslo-graben, which is a Permian rift basin consisting of different kinds of volcanic and sedimentary rocks. In the summer of 1998, approximately 300 samples of surface soil (2–3cm) were taken systematically, 1km^–2. The investigated area covers about 500km². Samples were dissolved in 7M HNO₃ and analysed for 29 elements with ICP-AES, mercury with cold-vapour technique (CV-AAS) and arsenic and cadmium with a graphite furnace (GF-AAS). A factor analysis is frequently used to identify relationships among sets of interrelated variables. To describe the covariant relationships among the elements, a factor analysis has been completed. The first factor contains the elements Sc, Fe, Li, Co, Al, Cr, Be, K, Ni, V, Mg, Y, Ba, Zr, Mn and As (listed with decreasing communality). These elements are typical for the minerals in the area and most of these elements have a near normal distribution. Sources for this factor are probably geological. The second factor contains Cd, Hg, P, Zn, Cu, Ba and Pb. They have a log-normal distribution. Road traffic is probably one of the sources contributing to this factor. In Norway studded tyres are used frequently in the winter season which results in large amounts of road dust. Leaded petrol has been a major source for Pb but is not in use any more. Wear and tear of tyres and brakes contribute also to this factor. Other sources contributing to this factor are probably industry, rubbish incineration, crematoria and release of some of these elements from structural material by fire. Factors 3, 4 and 6 with elements such as Ca, Na, La, Ti and Sr probably have geological sources. They are associated with minerals like amphiboles, pyroxenes and feldspars and some of the elements are from sea aerosols. Factor 5 contains Mn, Cd, Zn, As and Pb. Manganese may be derived from many different sources such as rock weathering, windblown dust, agriculture and traffic. Since As and Mn are placed in both factor 1 and 5 they probably have both geological and anthropogenic sources. Concentrations of the elements in the second factor are much higher in the central parts of Oslo, than in the rest of Oslo. The median value of Hg in the centre is 0.48mgkg^–1, which is 8 times higher than that in the rest of the city. Also, the other elements have much higher levels in the centre. The industrial district north-east of the centre also has high values. The distribution of arsenic is regular throughout the whole city, but has a slightly higher level in the centre. Norm values for contaminated land used by the Norwegian authorities are 2mg As kg^–1 and 25mg Cr kg^–1. Of 297 samples, 61% contain more than 25mg Cr kg^–1 and 79% more than 3mg As kg^–1, which is the detection limit of the analysis. These samples will therefore be regarded as contaminated. Factor analysis places these elements in the geological factor. The Norm value of zinc is 150mgkg^–1, and 40% of the samples contain more than this. The Norm value of lead is 150mgkg^–1, and 35% of the samples contain. Road traffic is probably the major source for these elements.     

Industry Response to the Challenge of Sustainability: The Case of the Canadian Nonferrous Mining Sector

/ The paper investigates how the Canadian nonferrous sector is tackling the challenge of sustainable development. Although there is no consensus as to what sustainable development means in practice for management in the sector, at least three dimensions must be taken into account: (1) metals are recyclable, the availability of this resource is not a concern for the foreseeable future; (2) the need to minimize environmental impacts of metals exploration, extraction, transformation, consumption, and recycling; and (3) production activities should not be socially or culturally disruptive. The nonferrous mining industry faces several environmental problems. Some of the most significant are acid mine drainage, sulfur emissions, recycling, and metals toxicity. The industry has developed a number of responses to address these specific concerns as well as other more general challenges. Six strategies are described and analyzed: (1) research and development, (2) an effort of consensus building among stakeholders known as the Whitehorse Mining Initiative, (3) international networking, (4) active involvement in the development of environmental management standards, (5) management reorganization and (6) voluntary agreements. The importance of external factors in the shaping of corporate environmental management practices is discussed, in particular the role of government. Progress has been achieved in three areas: (1) managerial practices and organization, (2) reducing the impacts of ongoing operations and (3) minimizing future liabilities, but two significant fields of conflict remain, namely mining in wilderness areas and projects on aboriginal lands.KEY WORDS: Canada; Environmental management; Minerals industry; Nonferrous metals; Sustainable development; Whitehorse Mining Initiative     

我国部分商品粮基地粮食重金属污染的差异分析与综合评价

本文根据1988年全国农业环境质量状况调查资料,选取我国部分商品粮基地县粮食重金属污染数据,通过多元统计分析,揭示了各商品粮基地粮食重金属污染的差异与分类。最后采用模糊综合评判方法,对各商品粮基地粮食重金属污染程度进行了综合评价,得到了相对污染程度的排序。     

高分子壳聚糖对微量金属离子的螯合作用研究

研究了壳聚糖对溶液中Mn2 + 、Fe2 + 、Cu2 + 、Zn2 + 4种常见微量金属离子的吸附作用 ,通过吸附率、溶液pH等参数 ,表征了壳聚糖的吸附能力及其对离子的选择性吸附 ,其选择性次序为 :Cu+ 2 >Zn2 + >Fe+ 2 >Mn+ 2 ,为壳聚糖处理污水中的微量金属离子作了探索。     

Rapid ecotoxicological assessment of heavy metal combined polluted soil using canonical analysis

IntroductionElevatedconcentrationofheavymetalssuchascopperandcadmiumexistinmanyagriculturalsoilsfromminingactivities(Chen ,2 0 0 0 ;Dudka ,1 997;Lambert,1 997)andfrommanagementpracticesincludingirrigationwithsewageandutilizationofsewagesludge(Clapp ,1 994) .Onceheavymetalsenteredintosoils,regardlessthesources,theywouldnotonlybeaccumulatedbyorganisms,butalsocirculateinthefoodchain (Uhlig ,2 0 0 0 ;Barcan ,1 998) .Furthermore ,theirramificationwouldberetainedinsoilecosystemwithtoxicconcentrati…     

初论元素富集成矿的地球化学机理—以岩浆热液矿床的形成为例

元素富集成矿的过程实质上是元素在地球不同圈层和不同相以及不同集合体之间分配的结果。元素的富集起始于地球形成的初期。对于大多数金属成矿元素 ,地壳特别是上地壳是大多数矿石和矿胎的储库 ,地壳丰度是元素富集成矿的物质基础。元素在地质体系演化共存相间的分配是元素富集成矿的关键过程。对于以侵入体为中心的热液矿床的形成 ,岩浆部分熔融、结晶分异、液态分离、挥发分分离以及气液相不混溶等过程能够导致金属元素最终达到矿石级的富集。挥发分则是元素富集成矿的重要制约因素     

不同土地利用类型下土壤特性及重金属评价

在哈尔滨市周家镇选择典型的五种土地利用类型(耕地、居民点及工矿用地、交通用地、林地、水域),24个样品,研究乡级小城镇不同土地利用类型下土壤特性及重金属状况.结果显示:(1)耕地的土壤理化性状最低,有机质与全氮有显著的正相关;(2)乡级小城镇不同土地利用类型下土壤中Zn、Pb含量存在显著差异,交通用地与耕地含量较高,同时各土地利用类型的内梅罗综合污染指数均达到中污染;(3)人类活动对土壤质量影响最大的是交通活动,其次是耕地施肥、使用农药及翻耕等,在次是居民生活.     

芝罘湾沉积物中可提取相重金属研究

讨论了芝罘湾沉积物酸提取相中Ｐｂ、Ｃｕ、Ｃｒ、Ｆｅ、Ｍｎ、Ｌｉ、Ｋ的分特征，及其在环境中的赋存形式，并与其它海区资料相比，得出该湾沉积物已受到重金属污染的结论。     

微生物与重金属的相互作用

从多方面概述了微生物与重金属的相互作用，重点描述了微生物对重金属的抗生和解毒作用，最后介绍了该研究领域发展前景。