基于生物导向的水生态健康监测及评估概述

环境监测是水生态健康监测与评估的重要环节,基于物理、化学监测的传统水质监测通常仅能提供独立的数据信息,不能全面、直观地反映水环境状况。基于生物等生命体导向的水生态监测通过生物对环境的响应,能够直接反应复杂水体状况,在水环境健康监测与评估中占据重要地位。基于病原微生物、指示生物介绍了生物监测中的常规生物指标,总结了包括藻类、无脊椎动物和鱼类在内的常见指示生物在不同类型污染水体中的环境指示作用。从生物毒性效应出发介绍了常用的毒性效应测试方法、分析了污染物在不同生物学水平的响应,从而指明生物毒性效应在水环境健康评估中的发展优势。再从生态完整性角度阐述了生态完整性评价的一般方法和新兴分子生物学技术在水生态健康评估中的应用。重点指出环境毒理学和分子生物学在水环境监测的优势,以期为更加科学精确地进行水生态健康监测预警提供支撑。     

新疆克州"十五"期间生态环境质量评价研究

区域生态环境状况对区域经济发展起重要支撑作用,本文采用遥感和地理信息系统的技术手段,利用2000年与2006年ETM影像及CBERS影像,结合《生态环境状况评价技术规范》中的技术方法,对克州"十五"前后生态环境状况进行了综合评价.研究认为,克州总体生态环境状况处于一般和较差水平,"十五"期间克州生态环境状况总体上虽无明显变化,但各生态环境状况评价指数基本上均呈现下降趋势.     

生态围隔对水源地水质的改善效果

采用渔网及土工布挂片双层材料以及填充的水花生构建了生态围隔,对藻类进行拦截,降低取水口藻类密度,同时通过水花生的吸收和拦截,以及土工布挂片形成的附着生物群落的降解和吸收作用,降低颗粒态以及溶解态营养盐,达到取水口水质的改善效果.生态工程实施后,取水口内悬浮颗粒物显著降低了29.8％,同时透明度提高了27.5％.对藻类的拦截效果研究表明,围隔对叶绿素a的去除率为23.0％,对总藻类数量的去除率为20.7％.通过对围隔内外蓝藻数量在藻类数量的比例分析,生态围隔对蓝藻的去除率高于总藻类的去除率,说明了对于藻类拦截的效果具有一定的选择性.对营养盐的改善效果主要体现在颗粒态物质上,其中颗粒态氮磷的去除率分别为48.4％和31.3％.     

盐城海滨湿地的生态风险评价方法

以盐城海滨湿地这一脆弱生态系统为对象进行了生态风险评价方法的探讨,针对其生态环境的特点,通过对盐城海滨湿地的环境问题的描述,分析了它的风险源、风险受体和评价终点,建立了盐城海滨湿地生态风险评价的评价指标体系,对其生态风险评价方法进行了探索。     

生态农业发展与小城镇建设

以3家生态村为例说明乡镇企业在生态农业产值中占据主导地位。通过对乡镇企业的经济效益、环境效益和社会效益以及小城镇发展的优越性分析可知，乡镇企业不宜在农村发展，应该在小城镇中发展，农村生态建设要立足农业，通过减少土地的人口承载量，提高劳动生产率和增加农民收入。     

齐齐哈尔市绿色食品产业发展的思考

阐明了绿色食品的内涵,产生的历史背景、客观原因,以及发展绿色食品对保障食品安全性、解决农产品国际贸易壁垒,实现农业可续发展的重大意义。在回顾齐齐哈尔绿色食品产生发展历程,目前取得的成效及存在的主要问题基础上,提出了加快齐齐哈尔绿色食品产生发展的思路与对策,着重强调要注重保护和发送生态环境,加强生产为基地建设,建设为龙头企业、加强市场开拓等关键性问题。     

An ecological economics approach to the management of a multi-purpose coastal wetland

Three interrelated management problems—eutrophication of multiple use shallow lakes, sea level rise and flood risk mitigation and tourism pressures—are analysed in the context of an internationally important wetland area, the Norfolk and Suffolk Broads in the UK. The ecological-economic research findings presented should provide essential information to underpin the regulatory and management process in this internationally important conservation area. The relevant authority somehow has to integrate the maintenance of public navigation rights, nature conservation, and tourism promotion in a highly dynamic ecosystems setting. Because of the stakeholder conflicts, potential and actual, a more inclusionary decision-making procedure is required, and is currently being implemented.     

Ecological analysis of disturbed riverbanks in the Montréal area of Québec

In revegetation trials on disturbed riverbank sites in the Montréal region (Québec, Canada), an analysis of their structure by means of their biotic and abiotic components was undertaken. Vegetation sampling and physical surveys, together with soil analyses of 62 stands, grouped in 20 sectors, were carried out in the summer of 1986. The statistical analyses of biotic and abiotic data were executed in parallel by a hierarchical agglomerative cluster analysis (arithmetic average clustering) and by an ordination in reduced space (principal coordinate analysis). The species colonizing these riverbanks are, for the most part, ruderals from the Montréal region, of which more than 50% are introduced species. The pioneering communities characterizing these artificial habitats have had very little impact on the physical conditions of their environment; therefore, the ordination on the plant communities proves to be strongly correlated to the ordination stemming from the abiotic components. The statistical analysis retains the original sectors, underlining the fact that each human intervention generally results in the creation of a particular ecological situation.     

Prioritizing ecological and human welfare risks from environmental stresses

The ecological systems of Earth are subjected to a wide array of environmental stresses resulting from human activities. The development of appropriate environmental protection and management policies and the appropriate allocation of resources across environmental stresses require a systematic evaluation of relative risks. The data and methodologies for comprehensive ecological risk assessment do not exist, yet we do have considerable understanding of econological stress-response relationships. A methodology is presented to utilize present knowledge for assignment of relative risks to ecological systems and human welfare from anthropogenic stresses. The resultant priorities, developed for the US Environmental Protection Agency's (EPA) relative risk reduction project, highlight global climate change, habitat alteration, stratospheric ozone depletion, and species depletion as the highest environmental risks, significantly diverging from the present emphasis by EPA and the public on toxic chemical issues. Enhanced attention to ecological issues by EPA and development of ecological risk assessment methodologies that value ecological and economic issues equitably are key recommendations.     

Arthropod community organization and development in pear

Arthropod communities in pear are conceptualized as hierarchically organized systems in which several levels of organization or subsystems can be recognized between the population level and the community as a whole. An individual pear tree is taken to be the community habitat with arthropod subcommunities developing on leaf, fruit, and wood subcommunity habitats. Each subcommunity is composed of trophically organized systems of populations. Each system of populations is comprised of a functional group or guild of phytophagous arthropods that use the habitat primarily for feeding but also for overwintering or egg deposition, and associated groups of specialized predators, parasitoids, and hyperparasitoids. Several species move from one subcommunity to another during the course of community development and thus integrate community subsystems. Community development or change in organization through time is conceptualized as being jointly determined by the development of the habitat and the organization of the species pool. The influence of habitat development on community development within a species pool is emphasized in this research. Seasonal habitat development is expressed as change in the kinds and biomasses of developmental states of wood, leaf, and fruit subcommunity habitats. These changes are accompanied by changes in the kinds, biomasses, and distributions of associated community subsystems.