国内外生态环境观测研究台站网络发展概况

生态环境观测研究台站是开展生态环境研究的重要手段。《国家环境保护"十二五"科技发展规划》将国家环境保护野外观测研究站作为"十二五"能力建设重点内容。分析了目前国内外主要生态环境监测网络,如区域尺度的全球环境监测系统(GEMS)、全球陆地观测系统(GTOS)、国际长期生态研究网络(ILTER)、全球通量观测网络(FLUXNET)和国际生物多样性观测网络(GEO·BON),以及国家尺度的美国长期生态研究网络(US-LTER)、英国环境变化监测网络(ECN)和中国生态系统研究网络(CERN)的发展历程、观测研究进展;总结了生态环境监测网站的发展趋势,即重视台站的联网观测研究,注重观测标准化和规范化及数据共享,重视观测手段智能化与自动化,注重综合观测与模型模拟相结合;提出国家环境保护生态监测台站网络是现有国家环境监测网络的拓展和完善,也是今后开展区域生态环境综合监测与评估的重要基础。     

日本国家尺度生物多样性监测概况及其启示

为保护地球生物资源，1992年巴西里约热内卢的联合国环境与发展大会签署《生物多样性公约》，1993年正式生效。公约第7条规定了缔约方有履行识别和监测需要保护的重要的生物多样性组成部分之义务。为此，全方位、多层次的生物多样性监测网络在世界各国家和地区得以建立和开展工作。日本作为《生物多样性公约》的缔约国之一，为履约并保护其国内因经济发展而受到严重威胁的自然环境和自然遗产，整合其20世纪70年代开展的“自然环境保护基础调查”和21世纪2003年开始构建的“重要地域生态系统监测网络”，逐步形成了国家尺度的生物多样性监测体系。根据日本生物多样性中心公布的信息与数据，介绍了日本国家尺度生物多样性监测的两项主要工作，即自然环境保护基础调查和重要地域生态系统监测网络；总结了日本国家生物多样性监测的发展历程和主要特点；提出了加强中国生物多样性监测工作的建议。     

山东省生物多样性试点评价

以县级行政区域为评价单元,利用现有文献资料和补充调查数据,按照《区域生物多样性评价标准》(HJ 623—2011)规定的评价指标和方法,评价了山东省120个县级行政区域的生物多样性状况,分析了生物多样性状况空间分布规律。评价结果表明:山东省县级行政区域生物多样性指数在23.27~40.24之间变化,县级行政区域生物多样性状况分为"中"和"一般",分别占山东省土地总面积的55.8%和44.2%。鲁中南山地丘陵区和鲁东丘陵区的生物多样性状况好于黄河三角洲、鲁西北和鲁西南平原区。     

江苏生物多样性保护进展、问题及对策建议

总结了江苏生物多样性保护管理工作取得的主要进展、典型做法及有益经验,分析了生物多样性现状特点,针对法规制度亟需加强、典型生境连通较差、基础能力尚显薄弱、物种入侵不容忽视、开发矛盾仍未根治等问题,提出,完善生物多样性管理政策制度、优化保护空间格局、加大自然生态系统保护修复、深化生物多样性本底调查评估、构建多级生物多样性观测网络、加强入侵物种监督管理、探索生物多样性可持续利用机制、提升生物多样性保护宣贯力度等对策建议,以期为新时期江苏生物多样性保护策略的制定提供参考和借鉴。     

《生物多样性公约》第十五次缔约方大会(COP15)主题发布

<正>9月3日,生态环境部部长李干杰与《生物多样性公约》(以下简称《公约》)执行秘书克里斯蒂娜·帕斯卡·帕梅尔共同发布《公约》第十五次缔约方大会(COP15)主题:"生态文明:共建地球生命共同体"。李干杰表示,这一主题顺应了世界绿色发展潮流,表达了全世界人民共建共享地球生命共同体的愿望和心声,彰显了习近平生态文明思想的鲜明世界意义。主题对引导国际社会保护生物多样性的政治意愿,推进全球生态文明建设,努力达成《公约》提出的到2050年实现生物多     

联合国《生物多样性公约》缔约方大会第十五次会议在云南昆明召开

正2021年10月11日,联合国《生物多样性公约》缔约方大会第十五次会议(COP15)第一阶段会议在云南昆明开幕。本次大会主题为"生态文明:共建地球生命共同体",大会于10月11日至15日和2022年上半年分两阶段在昆明召开,将全面总结国际社会在生物多样性保护方面的经验,谋划未来十年全球生物多样性治理蓝图,COP15也将成为《生物多样性公约》历史上具有里程碑意义的一次大会。     

重点生物物种保护率试点监测研究

为探索重点生物物种保护率监测方法并实践应用,选取昆山和射阳作为试点县域开展重点生物物种保护率监测研究。结果显示,共监测到重点生物物种87种,其中动物79种,植物8种。受威胁物种39种,其中极危物种5种,濒危物种19种,易危物种15种。重点保护物种79种,其中一级保护野生动植物28种,二级保护野生动植物51种;昆山和射阳的重点生物物种保护率分别为97.73%和100%。提出,为实现重点生物物种保护率监测工作的业务化运行,支撑重点生物物种和生物多样性保护管理,需要不断加强生物多样性观测能力建设,建立生物多样性监测长效机制,完善生物多样性物种信息数据库;各相关部门应统筹协调,整合资源,形成合力,实现重点生物物种、生物多样性和生态系统的监测、管理和保护的协调统一。     

江苏生物多样性保护的重点领域和政策创新

分析了江苏生物多样性保护现状,解读了省委办公厅、省政府办公厅《关于进一步加强生物多样性保护的实施意见》,主要涵盖完善政策法规、优化空间格局、提升系统稳定性、构建监测评估体系、提升安全管理水平、创新开发利用机制、严格执法监督评估、推动公众参与等8大工作任务,加强生态岛试验区、生态安全缓冲区等10大领域政策创新,整体提升全省生态系统质量。     

对国家环境保护野外观测研究站建设的几点思考

《国家环境保护"十二五"科技发展规划》提出将国家环境保护野外观测研究站作为"十二五"环境科技支撑能力建设内容之一;在《"十二五"国家自主创新能力建设规划》中也将国家野外科学观测研究站(网)作为科技创新基础条件的建设内容。在分析环保部门生态环境观测研究台站建设现状基础上,对国家环境保护野外观测研究台站的建设目标与定位、空间布局、运行机制、监测与评价技术体系构建、监测指标体系框架等进行分析探讨。在目标与定位上,国家环境保护野外观测研究台站既要与目前国内主要的生态环境监测网络(如中国生态系统研究网络和中国森林生态系统定位研究网络)形成补充,同时也要突出环保部门特色;在空间布局上既要关注水、空气、土壤污染的重点监控区,也要关注生态脆弱区、重要(点)生态功能区等生态敏感区;在技术体系上,要研究建立标准化、规范化的观测技术体系,同时也要注重生态环境评价方法研究,为生态环境精准化管理提供技术支持。     

新疆卡拉麦里山有蹄类自然保护区生物多样性保护研究

生物多样性具有多重价值,如生态价值、社会价值和经济价值。卡拉麦里山自然保护区生物多样性不但关系到当地经济发展和人民生存安全,而且关系到整个保护区、整个新疆的可持续发展。本文分析了卡拉麦里山有蹄类自然保护区生物多样性特点及生物多样性遭受严重破坏的原因,提出了保护该区生物多样性的对策措施：①加强卡拉麦里山有蹄类自然保护区生物多样性的调查研究工作。②加强保护区的建设。③加大立法与执法制度。④加强生物多样性保护的宣传教育。⑤加强生物多样性保护的公众参与。⑥加强当地居民的基本生产、生活条件建设。⑦在保护区推行生态旅游。     

Assessing Biodiversity

Environmental assessment and monitoring is not limited to measuringquantities of some substances that threaten our existence. Atpresent the greatest challenge is not to gain another decimal pointin assaying a certain noxious chemical. As far as technical aspectsof monitoring are concerned, we witness a steady progress. Ourconceptual development is less tangible. At the same time it ismore urgent. We are directed to assess and monitor novelcharacteristics such as biodiversity and ecosystem health. They areconsidered to be the basis of modern, ecosystem management.Specialists in wildlife, fisheries, soil scientists, agronomists,and foresters are revising the established tenets of theirdisciplines to pursue maximum biodiversity. This could be done onlyif we know what biodiversity and ecosystem health are. This paperassesses the state of our knowledge of these concepts.     

Atmospheric Change and Biodiversity

Strategies to conserve biodiversity need to include the monitoring, modelling, adaptation and regulation of the composition of the atmosphere. Atmospheric issues include climate variability and extremes; climate change; stratospheric ozone depletion; acid deposition; photochemical pollution; suspended particulate matter; and hazardous air pollutants. Coarse filter and fine filter approaches have been used to understand the complexity of the interactions between the atmosphere and biodiversity. In the first approach, climate-based models, using GIS technology, helped create future biodiversity scenarios under a 2 × CO₂ atmosphere. In the second approach, the SI/MAB forest biodiversity monitoring protocols helped calibrate the climate-forest biodiversity baseline and, as global diagnostics, helped identify where the biodiversity was in equilibrium with the present climate. Forest climate monitoring, an enhancing protocol, was used in a co-location approach to define the thermal buffering capacity of forest ecosystems and their ability to reduce and ameliorate global climate variability, extremes and change.     

Biodiversity and Saving the Earth

The challenges for reversing course in our stewardship of the earth's ecosystems has never been greater. Biodiversity is in decline on an unprecedented scale and it is tempting to use this as an indicator of the health of the earth's ecosystems. In fact it is one of a number of indicators that collectively provides information on trends in the condition of ecosystems. But the larger problem is the lack of integration between the social and natural sciences. Mainstream scientists continue to reject the notion that solving environmental problems requires an integration of values and processes. A conceptual model shows how these facets may be brought together. A holistic vision requires the integration of natural, social and health sciences. From this perspective the linkage between biodiversity, ecosystem resilience and management options is more clearly articulated.     

Atmospheric Change, Forests and Biodiversity

Predicted atmospheric change, mainly climate change, will have profound effects on the biodiversity of Canadian forests. Predictions derived from forest models, responses of species and ecosystems related to modern ecological characteristics and paleoecological studies suggest large-scale, wide-ranging changes from the biome to physiological levels. Paleoecological analogues in B.C. and other parts of Canada reveal that major changes must be expected in forest composition, range, structure and ecological processes. In B.C., past warmer and drier climates supported a different forest pattern, including forest types with no modern analogue. This produced dramatically different disturbance regimes, specifically more fires, and affected tree growth rates. The relationship of forests with non-forest habitats, especially wetlands and grasslands was different suggesting implications for wildlife biodiversity. British Columbia's Forest Practices Code prescribes guidelines for biodiversity objectives but ignores the issue of atmospheric change. This omission may result from a lack of understanding of the profound potential effects of atmospheric change on forest biodiversity in the next harvest cycle and lack of mechanisms to assess impacts and develop management strategies for specific sites. An example of a simple paleoecological assessment method involving pollen ratios is proposed.     

Towards a Simple Indicator of Biodiversity

Policy makers in Canada have suggested that the scientific community should develop an indicator of biodiversity change that can be implemented quite quickly without a major new investment in monitoring systems. We propose that such an indicator can be developed from the theory of species gradients in community ecology. The term 'species gradients' refers to the increasing diversity of species through time under stable conditions, and the increasing diversity of species with the increased use of available resources. This theory is reviewed under four different headings: evolutionary ecology, the energy theory, the resource productivity theory and the thermodynamic mechanism. The theoretical arguments provide a basis to propose detection of the 'leaky ecosystem' as an indicator of biodiversity. We propose that it is possible to detect the leaky energetics of ecosystems by means of routinely available observations of outgoing longwave radiation.     

A Systems Approach to Biodiversity Conservation Planning

With a recent media-fueled transition from a scientific to a political perspective, biodiversity has become an issue of ethics and ensuing values, beyond its traditional ecological roots. More fundamentally, the traditional perspective of biodiversity is being challenged by the emergence of a post-normal or systems-based approach to science. A systems-based perspective of living systems rests on the central tenets of complexity and uncertainty, and necessitates flexibility, anticipation and adaptation rather than prediction and control in conservation planning and management. What are the implications of this new perspective? This paper examines these challenges in the context of biodiversity conservation planning. The new perspectives of biodiversity are identified and explored, and the emergence of a new ecological context for biodiversity conservation is discussed. From the analysis, the challenges and implications for conservation planning are considered, and a systems-based or post-normal approach to conservation planning and management is proposed. In light of the new perspectives for biodiversity, conservation planning and management approaches should ultimately reflect the essence of living systems: they should be diverse, adaptive, and self-organizing, accepting the ecological realities of change.     

Atmospheric Change and Biodiversity in the Arctic

The Canadian Arctic is characterized by a high variation in landform types and there are complex interactions between land, water and the atmosphere which dramatically affect the distribution of biota. Biodiversity depends upon the intensity, predictability and scale of these interactions. Observations, as well as predictions of large-scale climate models which include ocean circulation, reveal an anomalous cooling of northeastern Canada in recent decades, in contrast to the overall significant increase in average annual temperature in the Northern Hemisphere. Predictions from models are necessary to forecast the change in the treeline in the 21st century which may lead to a major loss of tundra. The rate of change in vegetation in response to climate change is poorly understood. The treeline in central Canada, for example, is showing infilling with trees, and in some locations, northerly movement of the boundary. The presence of sea ice in Hudson Bay and other coastal areas is a major factor affecting interactions between the marine and terrestrial ecosystems. Loss of ice and therefore hunting of seals by polar bears will reduce bear and arctic fox populations within the region. In turn, this is likely to have significant effects on their herbivorous prey populations and forage plants. Further, the undersurface of sea ice is a major site for the growth of algae and marine invertebrates which in turn act as food for the marine food web. A rise in sea-level may flood coastal saltmarsh communities leading to changes in plant assemblages and a decline in foraging by geese and other consumers. The anomalous cooling in the eastern Arctic, primarily in late winter and early spring, has interrupted northern migration of breeding populations of geese and ducks and led to increased damage to vegetation in southern arctic saltmarshes as a result of foraging. It is likely that there has been a significant loss of invertebrates in those areas where the vegetation has been destroyed. Warming will have major effects on permafrost distribution and on ground-ice resulting in a major destabilization of slopes and slumping of soil, and disruption of tundra plant communities. Disruption of peat and moss surfaces lead to loss of insulation, an increase in active-layer depth and changes in drainage and plant assemblages. Increases of UV-B radiation will strongly affect vulnerable populations of both plants and animals. The indigenous peoples will face major changes in life style, edibility of food and health standards, if there is a significant warming trend. The great need is for information which is sensitive to the changes and will assist in developing an understanding of the complex interactions of the arctic biota, human populations and the physical environment.     

滨州沿海湿地生物多样性保护探讨

重点研究了该区域海洋生物多样性、淡水生物多样性、陆生和海岛等高等植物多样性、陆栖动物多样性与特点。分析了其破坏现状及原因，提出了生物多样性保护对策和可持续利用途径。     

Atmospheric Change and Biodiversity: Co-Networks and Networking

Canada responded to the Global Biodiversity Convention by completing the Canadian Biodiversity Strategy in 1995. At the same time, Environment Canada also completed a national Science Assessment on Biodiversity. During this period, the Smithsonian Institution, in partnership with Parks and Environment Canada, initiated the implementation of a global biodiversity monitoring program in Canada. Under the auspices of the United Nations Man and the Biosphere Program, the SI/MAB monitoring protocols and plots have spread across Canada at an unprecedented rate. National champions in the science and educational sectors, working within an inter-disciplinary ecological framework, have guided the development, education, quality control and sharing of atmosphere-biodiversity observations electronically.Atmospheric-Biodiversity Networks and Networking have traditionally operated within separate mandates with little degree of integration. Air-Bio Networks were designed within an integrated framework to better understand the atmospheric stress on biodiversity and the adaptation actions, nationally and regionally. Detailed examples of the cumulative effects of climate change, stratospheric ozone depletion, acid deposition, ground-level ozone, suspended particulate matter and hazardous air pollutants on biodiversity will be discussed using a Southern Ontario case study. In addition, recommendations will be presented for future paired SI/MAB plots, linked networks and networking for adaptation within the context of climate, chemical and ecological gradients.