乌海市发展循环经济初探

乌海市是资源型城市，生态环境恶劣，资源短缺将成为乌海市可持续发展的瓶颈，而大力发展循环经济将是破解这一瓶颈的唯一途径，也是乌海市未来社会经济持续增长的核心因素。本文旨在探讨中小型资源城市发展循环经济，在企业、园区、区域三个层面努力构建循环经济体系。     

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…     

采煤塌陷地复垦的环境经济分析——以开滦煤矿为例

将环境经济学引入复垦活动的分析和评价，着重考虑了复垦的生态社会效益，复垦土地资源的价值、市场价格变化对复垦经济收益的影响和复垦效益对时间的依赖性，以期为复垦项目的选择和相关政策的制定提供经济方面的依赖和指导。     

安徽省宁国市元竹枯死原因与防治对策研究

文章探讨了安徽省宁国市中溪镇元竹大面积枯死的原因.在现场调查、污染监测和综合分析的基础上,排除了污染、病虫害致死和元竹而开花死亡的可能性,得出该区元竹枯死是由于非污染生态工程道路改建、水利水电工程和河道采砂等人为活动所导致元竹区的局部生态系统破坏,致使该区地下水位的不正常变动,从而引起大面积不规则分布的元竹干枯或浸泡死亡.文中最后根据该区生态环境状况,给出了防治元竹枯死的生态对策与建议,为防治其它地区的元竹枯死提供了参考和经验.     

Compound contamination and secondary ecological effects of Cd and As in soil-alfalfa ecosystems

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过程耦合与空间集成：国土空间生态修复的景观生态学认知

新时期国土空间生态修复的核心是整体保护与系统治理,强调生态保护修复与社会经济发展耦合关联的系统性、协同性。景观生态学以景观为研究对象,基于整体综合视角聚焦景观结构与功能演变及其与人类社会相互作用机理,重点关注过程耦合与空间集成。面向国土空间生态修复的战略需求,景观生态学“格局与过程耦合-时空尺度-生态系统服务-景观可持续性”的研究路径能够为国土空间生态修复提供重要学科支撑;依据格局-过程互馈机理识别退化、受损的山水林田湖草生命共同体,基于景观多功能性权衡协调社会-生态需求并确定修复目标,应用生态安全格局优化多层级修复网络体系,建立面向景观可持续性的多尺度级联福祉保障。     

星云湖湖滨带生态建设与水生植被恢复

近年来由于人为活动的影响,星云湖的生态结构遭到了严重破坏,这是导致其污染自净能力下降,从而加速水质恶化的主要内在因素.在2000年3月湖泊水生生态演替调查及其原因分析的基础上,根据湖泊生态学的原理,提出了星云湖湖滨带生态建设与水生植被恢复的建设途径.     

Is renewable energy still green? Shaping Australia’s renewable energy enterprise in an age of ecological modernisation

ABSTRACT

Renewable energy (RE) illustrates well the logic of ecological modernisation (EM). This logic has successfully transformed RE from a fringe idea owned by largely environmental actors to a mainstream one embraced by a broader constituency. This mainstream embrace inevitably (re)shapes the renewables enterprise. Not all renewables actors today are driven by environmental goals. Instead, key actors, particularly in corporate or community domains, nurture competing norms and aspirations. How the renewables project is envisaged and the goals it is directed to serve can thus differ considerably. Understanding these differences is important since transformations in the energy domain will not only impact climate protection but shape social futures in significant ways. The analysis proceeds in two interrelated steps: first, empirically – conducting an exploration of some of the main projects and actors in the contemporary Australian RE space; and second, theoretically – considering these empirical developments through an EM lens.     

SBR活性污泥中的主要微生物类群及其基本生态规律初探

本文重点探讨采用ＳＢＲ活性污泥法处理有机磷农药（乐果）生产废水的工艺中，ＳＢＲ内的活性污泥的主要微生物类群、特征、功能以及与环境因子、废水处理运行状况的关系。     

Haloacetic acids in the aquatic environment. Part II: ecological risk assessment

Haloacetic acids (HAAs) are environmental contaminants found in aquatic ecosystems throughout the world as a result of both anthropogenic and natural production. The ecological risk posed by these compounds to organisms in freshwater environments, with a specific focus on aquatic macrophytes, was characterized. The plants evaluated were Lemna gibba, Myriophyllum spicatum and M. sibiricum and the HAAs screened were monochloroacetic acid (MCA), dichloroacetic acid (DCA), trichloroacetic acid (TCA), trifluoroacetic acid (TFA) and chlorodifluoroacetic acid (CDFA). Laboratory toxicity data formed the basis of the risk assessment, but field studies were also utilized. The estimated risk was calculated using hazard quotients (HQ), as well as effect measure distributions (EMD) in a modified probabilistic ecological risk assessment. EMDs were used to estimate HAA thresholds of toxicity for use in HQ assessments. This threshold was found to be a more sensitive measure of low toxicity than the no observed effect concentrations (NOEC) or the effective concentration (EC10). Using both deterministic and probabilistic methods, it was found that HAAs do not pose a significant risk to freshwater macrophytes at current environmental concentrations in Canada, Europe or Africa for both single compound and mixture exposures. Still, HAAs are generally found as mixtures and their potential interactions are not fully understood, rendering this phase of the assessment uncertain and justifying further effects characterization. TCA in some environments poses a slight risk to phytoplankton and future concentrations of TFA and CDFA are likely to increase due to their recalcitrant nature, warranting continued environmental surveillance of HAAs.