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1.
生物多样性监测指标体系构建研究进展   总被引:14,自引:1,他引:13  
陈圣宾  蒋高明  高吉喜  李永庚  苏德 《生态学报》2008,28(10):5123-5132
生物多样性监测是为确定与预期标准相一致或相背离的程度,而对生物多样性进行定期或不定期的监视,目前已成为生物多样性研究和保护的热点问题。生物多样性监测指标则是一些简化的生物或环境特征参数,说明生物多样性现状和变化趋势,以及人类活动压力对生物多样性的影响,以促进科学界、政府和公众间的沟通,提高生物多样性管理水平。近10年来,国际组织、政府机构和各国学者对生物多样性指标体系的构建进行了大量的探索工作,取得了很多进展,其中有些指标已经应用于实际监测项目。本文综述了生物多样性监测指标筛选的一般标准和指标体系构建的主要理论,梳理目前已提出或应用的主要生物多样性监测指标,以期为我国构建国家或区域尺度生物多样性监测指标体系提供参考。在此基础上分析提出:生物多样性概念的泛化、指标含义模糊以及知识和数据的缺乏是构建生物多样性监测指标的主要困难。我国未来的生物多样性监测指标体系构建需要关注以下两个方面:(1)紧密联系实际,构建适应性的监测指标体系,加强对典型生态系统区域的监测;(2)发展经济社会发展方面的指标,分析生物多样性变化的驱动力,为生物多样性保护和区域可持续发展提供科学依据。  相似文献   

2.
生物多样性评价工作是生物多样性保护的基础,而替代指标的应用是在环境影响评价中实现生物多样性快速评价的重要方法之一.本文介绍了生物多样性替代指标的概念,分析了不同生物类群之间广泛存在的相关性,总结了大尺度上兽类、鸟类、维管束植物物种数的经验比例(1:5:50).对目前可供使用的生物多样性替代指标进行了系统整理和分类,将其划分为生物类替代指标(包括指示类群、功能类群和珍稀濒危类群)和生境类替代指标(包括环境因子、景观格局和自然圣境).对不同指标的替代机理、有效性、使用方法和适用范围等进行了归纳,探讨了增强生物多样性替代指标应用有效性和评价精度的主要途径.研究可为保护地规划、生物多样性监测和环境影响评价等领域开展生物多样性快速评价,以及环境评价制度中生物多样性影响评价的完善提供参考.  相似文献   

3.
国际生物多样性研究科学计划与热点述评   总被引:13,自引:2,他引:11  
李延梅  牛栋  张志强  曲建升 《生态学报》2009,29(4):2115-2123
生物多样性与人类生活密切相关.近年来不断加剧的人类活动,对生物多样性造成了严重破坏.已有研究表明,地球上的物种正以前所未有的速度丧失.为了遏止这种状况,目前,世界上许多国际组织和国家都对生物多样性及其相关问题展开研究,并制定了与生物多样性保护相关的法规和战略计划,也采取了许多保护生物多样性的行动.DIVERSITAS是国际全球环境变化(GEC)四大研究计划之一,也是生物多样性领域最大的国际科学计划, DIVERSITAS于2001年开始启动了第Ⅱ阶段研究并确定了新的核心研究计划和跨学科交叉网络计划.世界自然保护联盟(The World Conservation Union,IUCN)在2008年发布了<塑造可持续的未来:IUCN 2009~2012年计划>,提出了5个优先主题领域.欧盟于2006年通过了一项保护生物多样性的新战略--<2010年及未来阻止生物多样性丧失:人类福祉的可持续生态服务>.此外,很多国际/国家基金组织还发起了一些全球性的生物多样性计划,如国际海洋生物普查计划、生命之树计划、国际生命条码计划等.本文对上述生物多样性保护和研究的国际计划予以概要介绍和评述,并指出当前国际上生物多样性研究的主要热点,即:生物多样性变化与生态系统功能;生物多样性和生态系统服务的价值评估;生物多样性与气候变化;生物多样性长期动态监测;生物多样性的评价指标等.  相似文献   

4.
陆域生物多样性综合评估是保护生物多样性的重要基础工作,评估生物多样性现状和变化趋势、分析其损失的影响因素,是制定生物多样性保护政策与措施的前提和必要条件。目前,我国在陆域生物多样性综合评估方面尚未形成统一的评估指标体系。本研究围绕《生物多样性公约》爱知生物多样性目标、联合国可持续发展目标,借鉴国际上生物多样性评估新趋势,基于压力-状态-响应(PSR)概念框架,构建了我国陆域生物多样性综合评估指标体系,确定了22项评估指标,其中状态指标8项,压力指标7项,响应指标7项,并对指标相关性和可获得性进行分析。指标体系不仅可以对陆域生物多样性基本状况、受威胁程度、保护成效进行单独定量评价,还可以用于陆域生物多样性综合定量评估,以优化调整生物多样性优先保护区和保护措施。本研究可以为管理部门核算绿色国内生产总值(GDP)、制定区域生态补偿政策等提供技术支撑。  相似文献   

5.
长江上游是我国生物多样性最丰富的地区之一,也是全球生物多样性热点地区之一.准确可靠地掌握生物多样性信息是生物多样性保护科学决策的基础,大尺度的生物多样性保护重要性评估已成为生物多样性研究及其保育管理和决策最紧迫的问题之一.设计了由植被景观多样性指数、自然保护区多样性指数、基于生态系统类型的物种多样性指数、国家保护植物多样性指数和国家保护动物多样性指数5大指标构成的区域生物多样性综合评价指标体系及其计算公式,并以县域为评价单元,开展了长江上游生物多样性综合评价.结果表明,长江上游生物多样性保护重要性评价结果为极重要的县域共18个,占总县数的4.95%;评价结果为重要的县域共41个,占11.26%;评价结果为次重要的县域共76个,占20.88%;评价结果为中等水平的县域共106个,占29.12%;评价结果为中下水平的县域共68个,占18.68%;评价结果为不重要的县域共55个,占15 11%.长江上游生物多样性保护重要性评价结果为极重要、较重要和重要的县域主要分布于横断山区、秦巴山区、华西雨屏区、长江源区和川渝鄂黔交界处山地.  相似文献   

6.
全球生物多样性监测及其进展   总被引:7,自引:0,他引:7  
全球生物多样性监测及其进展曹志平(中国农业大学资环学院生态系,北京100094)钟晓东(国家环保局国际合作司,北京100035)1背景生物多样性监测最主要的目的是为管理者和决策者服务[1],为他们在保护生物多样性、制定土地利用规划、评价环境影响等问...  相似文献   

7.
生物多样性的稳定维持关乎人类生存发展与地球健康。生物多样性核心监测指标(Essential Biodiversity Variables, EBVs)旨在结合地面调查与遥感技术, 为大尺度、长时间序列的生物多样性监测提供新的解决方案。然而, 目前学界仍然缺乏一套国家尺度标准化EBVs遥感监测产品数据集, 以进行生物多样性评估。本研究旨在对中国生物多样性核心监测指标遥感产品进行体系构建与思考, 首先综述了目前EBVs的遥感研究概况, 并根据EBVs研究文献的数量进行调研分析; 同时, 本文在已有遥感生物多样性产品优先标准的基础上, 添加了“可重复性”的新标准, 并据此构建了中国EBVs遥感产品体系与监测数据集的指标清单, 最终对中国EBVs遥感研究存在的问题进行思考与讨论。本研究可为中国的生物多样性遥感监测提供科学依据, 有望为中国生物多样性政策的制定提供支撑。  相似文献   

8.
森林生物多样性的保护和持续利用是森林可持续经营的重要内容,如何快速有效地评价生物多样性是当前森林经营实践中面临的重要问题。本文以可持续发展为指导思想,针对阔叶红松林区森林可持续经营中的生物多样性保护问题,提出了一套生物多样性间接评价的体系和评价方法。生物多样性间接评价的基本原理是以物种与生境的关系、森林自然干扰状况、物种间的相互关系和对特殊生境及敏感物种的考虑等为基础的。依据阔叶红松林区的干扰状况、林分一般状况、立木层、灌木层、草本层、附生植物和藤本植物等的特点,采用重复累加的方法,制定了阔叶红松林区林分生物多样性间接评价的打分表。在一个森林经营单位(林业局或林场)进行生物多样性的保护时,首先应根据不同森林类型对干扰的适应和抵抗力大小确定对各类森林优先保护的次序,然后再在各类森林的不同小班中进行生物多样性间接评价打分表的填写,最后根据不同小班生物多样性得分的多少确定其保护的等级或先后次序。生物多样性间接评价调查可以结合森林经理调查来进行。  相似文献   

9.
中国森林生物多样性保护和恢复措施的制订依赖于生物多样性的监测信息。设计一个有效的生物多样性监测网络是一项复杂的系统工程。监测网络的设计框架可分为监测目标、监测对象、监测指标、取样策略、数据采集和处理、网络维护以及组织工作等几个部分。目前, 国际上已有5个得到广泛认可的生物多样性监测网络, 包括地球观测组织-生物多样性监测网络、全球森林监测网络、热带生态评估与监测网络、泛欧洲森林监测网络和亚马逊森林清查网络, 它们的监测目标、监测内容和方法、样地布局及部分监测成果各有特色。我们试图在全国生物多样性监测、森林资源清查和森林生态系统定位研究的基础上, 通过网络布局、建设和运行, 形成中国森林生物多样性监测网(Chinese Forest Biodiversity Monitoring Network, Sino BON-CForBio)及其监测规范体系。该网络的科学目标是, 在全国尺度上研究不同典型地带性森林的生物多样性维持机制、监测森林生物多样性变化并阐明其机理、研究生物多样性变化的效应。该网络布局以《中国植被区划》中的森林植被区划成果作为顶层设计和监测样地选择的核心依据, 设计了4个层级的监测系统; 其监测指标体系以生物多样性核心指标为主, 并结合我国传统森林群落调查方法进行拓展; 预期建成国家水平上的森林生物多样性监测网络, 阐明森林生物多样性维持机制和生物多样性变化的效应, 同时对重大生态保护工程的生物多样性保护效果进行有效性监测和验证型监测。  相似文献   

10.
唐得昊  邹欣庆  刘兴健 《生态学报》2013,33(4):1240-1250
生态系统健康评价是生态系统保护和监测研究的重要内容,该过程迫切需要综合性强、准确性高的指标,能质和生物多样性指标都是生态系统健康评估中的有效指标.以江苏省海岸带游泳和底栖生物群落为对象,沿海岸线从海州湾到长江入海口北岸选取15个站点,调查研究江苏省海岸带生态系统能质和生物多样性及其空间分布格局.结果表明:江苏海岸带除了中部地区能质和结构能质值较一致(都偏小)外,南北差异明显,生物多样性指数空间分布情况为南部Margalef指数略大于北部,中部较小,Shannon Wiener和Simpson指数空间分布都为南部>中部>北部;能质与生物多样性指标在高级生态系统中反映的生态系统健康状态一致,在中低级生态系统中差异明显;能质与生物多样性指标关联程度低,前者的测算侧重于生态系统中物种的等级,后者的测算侧重于物种的数量;总结能质和生物多样性指标在理论支撑、建立理论视角、与生态系统健康对应关系、应用模型以及局限性等方面的差异,研究结果在一定程度上可以丰富和完善生态系统健康评价研究理论与方法体系.  相似文献   

11.
Rigorous and widely applicable indicators of biodiversity are needed to monitor the responses of ecosystems to global change and design effective conservation schemes. Among the potential indicators of biodiversity, those based on the functional traits of species and communities are interesting because they can be generalized to similar habitats and can be assessed by relatively rapid field assessment across eco-regions. Functional traits, however, have as yet been rarely considered in current common monitoring schemes. Moreover, standardized procedures of trait measurement and analyses have almost exclusively been developed for plants but different approaches have been used for different groups of organisms. Here we review approaches using functional traits as biodiversity indicators focussing not on plants as usual but particularly on animal groups that are commonly considered in different biodiversity monitoring schemes (benthic invertebrates, collembolans, above ground insects and birds). Further, we introduce a new framework based on functional traits indices and illustrate it using case studies where the traits of these organisms can help monitoring the response of biodiversity to different land use change drivers. We propose and test standard procedures to integrate different components of functional traits into biodiversity monitoring schemes across trophic levels and disciplines. We suggest that the development of indicators using functional traits could complement, rather than replace, the existent biodiversity monitoring. In this way, the comparison of the effect of land use changes on biodiversity is facilitated and is expected to positively influence conservation management practices.  相似文献   

12.
In view of better linking conservation and sustainable development, it is imperative to optimize the transfer of biodiversity-related knowledge and technology from resource-rich countries to developing countries. All countries signatory to the Convention on Biological Diversity are expected to report on their progress towards achieving the Aichi Biodiversity Targets. However, weak data coverage and the technicality or even unavailability of indicators present major barriers to the monitoring of biodiversity as well as the development of adequate biodiversity policies and management plans in many countries of the global South, hence increasing the North-South knowledge and capacity gap. Capacity development in these countries may hence substantially enrich global biodiversity monitoring and policy. In this effort, ensuring that monitoring programs are realistic and sufficiently embedded in policy remains a challenge. To contribute to the mainstreaming of biodiversity into development cooperation, we developed a capacity development concept that links scientific data to policy development. To guarantee shared ownership, academic institutes and organisations or authorities with responsibilities in biodiversity policy were invited to jointly submit competitive “Monitoring, Reporting and Verification” (MRV) project applications. It appeared that especially ground truthing, economic valuation of biodiversity, and the application of modern technologies in biodiversity monitoring were missing capacities in the global South. Efforts are also required to increase the understanding and use of indicators to avoid them remaining a theoretical concept. As is observed with MRV in the carbon context, increased involvement of local communities is recommended in the global MRV framework, including techniques such as community-based Mapping, Measuring and Monitoring.  相似文献   

13.

Global biodiversity monitoring systems through remote sensing can support consistent assessment, monitoring, modelling and reporting on biodiversity which are key activities intended for sustainable management. This work presents an overview of biodiversity monitoring components, i.e. biodiversity levels, essential biodiversity variables, biodiversity indicators, scale, biodiversity inventory, biodiversity models, habitat, ecosystem services, vegetation health and biogeochemical heterogeneity and discusses what remote sensing through Earth Observations has contributed to the study of biodiversity. The technological advancements in remote sensing have enabled information-rich data on biodiversity. Remote sensing data are making a strong contribution in providing unique information relevant to various biodiversity research and conservation applications. The extensive use of Earth observation data are not yet realized in biodiversity assessment, monitoring and conservation. The development of direct remote sensing approaches and the techniques for quantifying biodiversity at the community to species level is likely to be a great challenge for comprehensive earth observation-based monitoring strategy.

  相似文献   

14.
According to the Millennium Ecosystem Assessment, common indicators are needed to monitor the loss of biodiversity and the implications for the sustainable provision of ecosystem services. However, a variety of indicators are already being used resulting in many, mostly incompatible, monitoring systems. In order to synthesise the different indicator approaches and to detect gaps in the development of common indicator systems, we examined 531 indicators that have been reported in 617 peer‐reviewed journal articles between 1997 and 2007. Special emphasis was placed on comparing indicators of biodiversity and ecosystem services across ecosystems (forests, grass‐ and shrublands, wetlands, rivers, lakes, soils and agro‐ecosystems) and spatial scales (from patch to global scale). The application of biological indicators was found most often focused on regional and finer spatial scales with few indicators applied across ecosystem types. Abiotic indicators, such as physico‐chemical parameters and measures of area and fragmentation, are most frequently used at broader (regional to continental) scales. Despite its multiple dimensions, biodiversity is usually equated with species richness only. The functional, structural and genetic components of biodiversity are poorly addressed despite their potential value across habitats and scales. Ecosystem service indicators are mostly used to estimate regulating and supporting services but generally differ between ecosystem types as they reflect ecosystem‐specific services. Despite great effort to develop indicator systems over the past decade, there is still a considerable gap in the widespread use of indicators for many of the multiple components of biodiversity and ecosystem services, and a need to develop common monitoring schemes within and across habitats. Filling these gaps is a prerequisite for linking biodiversity dynamics with ecosystem service delivery and to achieving the goals of global and sub‐global initiatives to halt the loss of biodiversity.  相似文献   

15.
科学制定生物多样性保护和恢复政策, 需要空间上连续、时间上高频的物种和生境分布以及物种迁移信息支持, 遥感是目前能满足该要求的有效技术手段。近年来, 遥感平台和载荷技术高速发展, 综合多平台、多尺度、多模式遥感技术, 开展基于站点的星空地一体化遥感观测试验, 可以对地表进行时空多维度、立体连续观测, 为生物多样性遥感监测提供了新的契机。本文总结了使用遥感技术监测生物多样性的主要方法, 回顾了典型的星空地一体化遥感观测试验。综述以往研究发现, 一方面, 现有遥感试验还缺少对生物多样性直接监测指标的观测, 另一方面, 生物多样性遥感监测方法也缺少星空地多维立体观测平台的支撑, 亟需加强两者的融合, 开展基于站点的生物多样性星空地一体化遥感监测研究。以设于我国四川王朗大熊猫国家级自然保护区内的王朗山地生态遥感综合观测试验站为例, 展示了星空地一体化遥感综合观测试验平台在生物多样性监测中的应用潜力。星空地一体化遥感观测可以提供物种和生境的综合定量信息, 与生态模型有机结合, 可以刻画生物多样性的时空格局与动态过程, 有助于挖掘过程机理, 提高生物多样性监测的信息化水平。  相似文献   

16.
Towards the global monitoring of biodiversity change   总被引:13,自引:0,他引:13  
Governments have set the ambitious target of reducing biodiversity loss by the year 2010. The scientific community now faces the challenge of assessing the progress made towards this target and beyond. Here, we review current monitoring efforts and propose a global biodiversity monitoring network to complement and enhance these efforts. The network would develop a global sampling programme for indicator taxa (we suggest birds and vascular plants) and would integrate regional sampling programmes for taxa that are locally relevant to the monitoring of biodiversity change. The network would also promote the development of comparable maps of global land cover at regular time intervals. The extent and condition of specific habitat types, such as wetlands and coral reefs, would be monitored based on regional programmes. The data would then be integrated with other environmental and socioeconomic indicators to design responses to reduce biodiversity loss.  相似文献   

17.
Land-use and climate change are major threats to biodiversity and ecosystem functions. Most of the current biodiversity monitoring systems are based on periodic records of the populations of a set of threatened or popular ‘flagship’ indicator species. In contrast to the abundance-based monitoring of species, also specific indicators of processes and functional interactions in an ecosystem may become targets of a more functional monitoring which can unveil early responses of an ecosystem to environmental changes at different spatial and temporal scales. The contributions of this Special Issue present such functional indicators for assessing and predicting responses to environmental changes of ecosystem functions in a hotspot of tropical biodiversity.  相似文献   

18.
外来生物入侵是继生境破坏后造成生物多样性丧失的第二大威胁因素, 已对入侵地的生态安全、经济和社会发展及人类健康等造成严重负面影响, 成为21世纪五大全球性环境问题之一。作为水产养殖、航运和水生宠物交易大国, 我国水生生态系统的生物入侵问题尤为严重。研究表明, 系统地构建并应用早期监测预警技术是防控水生生态系统生物入侵最有效的途径。和陆生生物相比, 水生生物群落的物种繁多、群落结构复杂、生物形体微小且在入侵初期群体规模极小、隐匿于水下、可用于物种鉴定的外部形态缺乏, 使得在水生生态系统中构建并应用早期监测和预警体系在技术层面更具挑战。随着高通量测序技术的快速发展, 环境DNA-宏条形码技术成为构建水生生态系统入侵生物早期监测与预警技术的首选。本文主要综述了基于环境DNA-宏条形码技术的水生生态系统入侵生物的早期监测与预警技术方法; 解析了环境DNA-宏条形码监测系统的应用现状、技术优势; 着重探讨了影响监测结果准确性的I型和II型错误及其产生原因, 并为避免两类错误提供了可行的优化/改进方案; 最后对该方法在水生入侵生物监测中的应用前景进行了展望。  相似文献   

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