Comparing aquatic risk assessment methods for the photosynthesis-inhibiting herbicides metribuzin and metamitron

Three different risk assessment procedures are described that aim to protect freshwater habitats from risks of the photosynthesis-inhibiting herbicides metribuzin and metamitron. These procedures are (1) the first-tier approach, based on standard toxicity tests and the application of an assessment factor, (2) the Species Sensitivity Distribution (SSD) approach, based on laboratory tests with a wider array of species and the application of a statistical model to calculate the HCx (the Hazardous Concentration for x% of the species), and (3) the model ecosystem approach, based on the evaluation of treatment-related effects in field enclosures. A comparison of the risk assessment procedures reveals that the first-tier approach is the most conservative for metamitron and metribuzin, and that HC5 values (and even HC10 values) based on acute EC50 values of algae and aquatic vascular plants may be used to derive maximum permissible concentrations for single applications. For both compounds these HC5 values were very similar to the ecological threshold concentrations in the enclosure studies. In contrast to model ecosystem experiments, however, HCx values based on lab toxicity tests do not provide information on the recovery potential of sensitive endpoints and on indirect effects, which may be important for regulatory decision-making. In the enclosure study, indirect effects of metribuzin on invertebrate populations were observed at an exposure concentration that was approximately 20 times lower than the corresponding HC5 value based on lab toxicity data for aquatic invertebrates.     

铁路取弃土场生态恢复调查分析

选择我国不同地域6条铁路,现场调查铁路取土、弃土(渣)场的使用及恢复情况,从取弃土场的占地面积及类型、取土量、弃土量等方面分析了其利用现状,并对植被恢复效果和难易程度进行了讨论。调查表明:北方平原区、荒漠区铁路的取土量较多,南部丘陵区的弃土(渣)场及弃渣量较多。从恢复效率和程度看,南部地区植被恢复相对容易且在1年内可以恢复到较好程度,但植被恢复不到位,较易发生水土流失等次生灾害;东北、华北地区植被恢复2年左右可以恢复至良好程度;西北地区植被恢复需求较小;对于部分高原地区,海拔越低、降雨越多,恢复越好,但部分地区降雨量是生态恢复的首要制约因子,保水措施是这类地区生态恢复的重点。     

生态补偿研究现状与进展

回顾和总结了国外生态补偿理论研究和实践发展状况,指出为我国建立生态补偿机制的借鉴作用,分析了我国生态补偿研究现状和实践进程。得出我国生态补偿在理论和实践层面还有需要加强和完善之处,最后提出我国生态补偿研究的主要方向。     

生态建设补偿机制的框架构建

生态补偿机制目前是国内外研究的热点,生态建设补偿机制是生态补偿机制的重要组成部分。本文首先分析了生态建设补偿机制的内涵,研究构建了生态建设补偿机制的框架。     

环境污染对生态危害经济损失风险评估模式的综述

从风险评价和环境经济学角度,综述了环境污染对生态环境危害经济报失的评估模式。     

多途径实现城市垃圾无害化处理

从多方面分析了城市垃圾对环境、对人类健康造成的危害,以及在垃圾处理过程中形成的二次污染。并提出了相应的对策,以实现城市垃圾的无害化处理。     

开发区土地生态适宜度评价探讨-以淮安外向型农业综合开发区为例

本文以淮安外向型农业开发区为研究对象,在开发区的环境影响评价和环境保护规划中引入土地利用生态适宜度评价的方法,在详尽调查研究的基础上,选择相应的评价因子,建立开发区生态适宜度评价指标体系,并借助GIS技术将数值计算和图形叠置有机结合,为开发区的合理规划提供决策依据。     

生态足迹方法在县级城市的运用--以成都市龙泉驿区为例

本文以成都市1999年和2003年统计年鉴和龙泉驿区统计年鉴1998年和2003年的数据为依据,采用生态足迹的方法,对龙泉驿区1998年和2003年的可持续发展性进行定量评价,通过计算和分析,结果表明龙泉驿区1998年和2003年人均生态足迹均为赤字,且2003年比1998年的生态足迹赤字更为加剧,这反映出人类的生产、生活强度超过了生态系统的承载能力,此区域生态系统处于过度开发利用和压力之下,随着经济的发展,人口的增加,这种趋势还在继续加大.     

沙湾荒漠区生态环境的植物监测

利用植物生态学常规方法进行了荒漠植被种群生物量和数量特证调查,以植物为监测对象,并就群落地上部分生物量,Shannon-Wiener多样性指数,群落均匀度,生态优势度等指标探讨了在荒漠生态环境监测和评价中的具体应用。     

Soft intervention technology as a tool for integrated coastal zone management

After introducing soft defence techniques as an alternative to hard defence techniques, the need is emphasized to consider the coastal area as an integral system. By recalling the main driving factors for coastal management: conflict resolution, resilience and sustainability, we logically arrive at the concepts of ecological engineering and ecotechnology, which are increasingly acknowledged as possible solutions to achieve sustainable use of coastal space as a resource. In this context, we refer to the principles of self design and of ecosystem conservation. In order to deal with real situations we are in need of fundamental ‘tools’ for the application of the soft intervention technology approach. We therefore introduce the concept of physiographic units and develop an initial elaboration for a coastal stretch and for coastal wetlands. The latter deserve more attention because of the already established practices of ecotechnology, at least as far as water and soil quality are concerned, but certainly also concerning morphology, especially in the future. We conclude by briefly discussing how activities undertaken in two research projects currently being conducted under the framework of the Marine Science and Technology Program of the Commission of the European Communities are expected to contribute to the concepts introduced here.