生态系统红色名录——一种新的生物多样性保护工具

生物多样性为人类提供了生存所必需的一系列生态系统服务和功能。然而,由于人为活动的加剧,生物多样性不断丧失。传统的生物多样性保护主要关注物种多样性,存在着对生物多样性的代表性不足,不能及时反应生态系统多样性的变化等缺点。近年来,生态系统层次上的多样性保护成为研究热点,一些国家和组织相继开展了大尺度的生态系统评估工作。文章回顾了已有的生态系统评估方案,发现当前生态系统评估多采用IUCN物种红色名录的分级标准体系,主要评估生态系统的濒危程度,评估标准主要是分布范围和功能的变化,不同评估方案采用的指标和阈值有差异,需要建立统一的生态系统分类体系和评价方案。同时,结合国内生态系统评价的现状,提出了在我国开展生态系统红色名录研究的若干可行建议。     

基于信息网络模型的生态风险评价

人类开发活动造成剧烈的生态系统自然条件变化,生态风险评价可以对受到人为干扰下生态系统(包括物种和群落等)的潜在影响进行模拟和量化。通过对信息流量的概念和网络控制分析,综合考虑生态系统组分间的直接和间接作用,提出一种能实现全局风险模拟的生态网络模型,即信息网络模型。在该模型基础上,建立了面向整体生态系统的生态风险评价框架,同时实现兼容多胁迫因子统一模拟和多风险受体间的风险追踪。以澜沧江漫湾水库为例,在估算重金属Hg、Pb和Cd初始环境风险后,利用信息网络模型追踪分析生态系统中不同生态功能组分之间的风险传递路径,评估各生态组分和整体系统的危险程度。结果表明,在累积效应作用下,对于生态系统和部分群落,整合网络风险值与初始环境风险值之间有着显著差别;在发生环境胁迫时,虽然处于食物网底层的生物类群可能最先受险,但在控制信息作用下食物网上层类群也会受险,甚至其最终受到的潜在威胁比前者更大。信息网络模型可识别出复杂的风险流动路径和群落间的风险累积,从而为生态系统风险评价和管理提供更为系统综合的理论依据。     

基于多风险源胁迫的西南地区生态风险评价

西南地区生态环境复杂、人地矛盾突出,生态系统面临着多种风险胁迫,进行生态风险评价对区域生态风险的预警和防控具有重要的意义。基于西南地区的生态环境特征,将生态风险分为自然灾害风险与人类活动风险,从风险源危险性、生态系统潜在损失度、生态系统易损性3个方面构建单一风险评价模型,将单一风险评价结果进行综合分析得到西南地区综合生态风险结果。研究表明,西南高生态风险区面积为17.02万km2,占研究区总面积7.4%,主要分布在念青唐古拉山、邛崃山、哀牢山、无量山、金沙江、怒江、澜沧江、大渡河流域等地,以及成都、重庆、贵阳等人地作用强烈的大城市周边。这些地区环境复杂,灾害易发,应加强防控与监测,优化产业结构,继续推进生态保护工程,降低生态风险。     

城市生态风险评价研究进展

随着城市化发展和城市人居环境的恶化,城市生态风险越来越受到关注,但尚缺乏有关城市生态风险评价的深入系统研究.本文依据城市生态学原理及生态风险评价框架从驱动力、风险源、风险受体与评价终点,以及生态风险综合评价方法等方面对城市生态风险评价研究进行综述.指出城市经济社会活动类型与程度是城市生态风险产生的主要驱动力;城市生态系统不同等级功能实体和城市整体是城市生态风险评价中的风险受体;城市生态风险评价终点包括城市生态系统结构、过程、功能要素,以及城市整体水平的性质和功能变化;耦合了社会经济需求的生态系统模型是城市生态风险评价方法的发展方向.未来城市生态风险评价研究应明确生态风险管理具体目标,确定综合性评价终点,建立多指标评价体系和综合评价方法.     

Native and alien plant species richness in relation to spatial heterogeneity on a regional scale in Germany

Aim The aim of our study was to reveal relationships between richness patterns of native vs. alien plant species and spatial heterogeneity across varying landscape patterns at a regional scale. Location The study was carried out in the administrative district of Dessau (Germany), covering around 4000 km². Methods Data on plant distribution of the German vascular flora available in grid cells covering 5′ longitude and 3′ latitude (c. 32 km²) were divided into three status groups: native plants, archaeophytes (pre 1500 AD aliens) and neophytes (post 1500 AD aliens). Land use and abiotic data layers were intersected with 125 grid cells comprising the selected area. Using novel landscape ecological methods, we calculated 38 indices of landscape composition and configuration for each grid cell. Principal components analysis (PCA) with a set of 29 selected, low correlated landscape indices was followed by multiple linear regression analysis. Results PCA reduced 29 indices to eight principal components (PCs) that explained 80% cumulative variance. Multiple linear regression analysis was highly significant and explained 41% to 60% variance in plant species distribution (adjusted R²) with three significant PCs (tested for spatial autocorrelation) expressing moderate to high disturbance levels and high spatial heterogeneity. Comparing the significance of the PCs for the species groups, native plant species richness is most strongly associated with riverine ecosystems, followed by urban ecosystems, and then small‐scale rural ecosystems. Archaeophyte and neophyte richness are most strongly associated with urban ecosystems, followed by small‐scale rural ecosystems and riverine ecosystems for archaeophytes, and riverine ecosystems and small‐scale rural ecosystems for neophytes. Main conclusions Our overall results suggest that species richness of native and alien plants increases with moderate levels of natural and/or anthropogenic disturbances, coupled with high levels of habitat and structural heterogeneity in urban, riverine, and small‐scale rural ecosystems. Despite differences in the order of relevance of PCs for the three plant groups, we conclude that at the regional scale species richness patterns of native plants as well as alien plants are promoted by similar factors.     

国家公园生态系统健康测度模型构建及黄山实证研究

国家公园是中国生态文明建设的重要制度实践,其生态系统健康的科学评估是国家公园分区管理、空间管制、生态保护的基础。国家公园生态系统具有特殊性和复合性,区别于城市、流域、湿地等生态系统,亟需建立一套适合国家公园生态系统的生态系统健康测度模型。基于国家公园生态系统的特殊性和生态系统健康概念的多维性,探讨了现有模型存在的问题和不足,从生态系统与人类活动交互的视角,建立了"VSR"(生态活力Vigor、服务能力Service、抗干扰力Resilience)国家公园生态系统健康测度模型。此外,将"VSR"模型应用到黄山国家公园生态系统健康的测度中,可视化了黄山国家公园生态系统健康的时空过程和格局,通过随机森林回归模型和增强回归树模型验证了"VSR"模型的有效性和稳定性。"VSR"国家公园生态系统健康测度模型有效量化了国家公园生态系统健康的时空差异性和时空动态性,为国家公园空间管制、生态保护等目标实施提供了科学支撑。     

Vital Landscape Attributes: Missing Tools for Restoration Ecology

Twenty-three “vital ecosystem attributes” (VEAs) were previously proposed to aid in quantitative evaluation of whole ecosystem structure, composition, and functional complexity over time. We here introduce a series of 16 quantifiable attributes for use at a higher spatial scale and ecological organizational level, the landscape. “Vital landscape attributes” (VLAs) should be useful in evaluating the results of ecological restoration or rehabilitation undertaken with a landscape perspective, provided that clear definitions and boundaries are agreed upon for the different spatial and ecological entities involved. Like VEAs, VLAs should be sensitive to changes wrought by human as well as to nonhuman factors leading to ruptures in flow processes or vegetation “switches.” They should be applicable over a wide range of landscape types and therefore aid in conducting rigorous interlandscape comparisons. We present three groups of VLAs: (1) landscape structure and biotic composition, (2) functional interactions among ecosystems within the landscape, and (3) degree, type, and causes of landscape fragmentation and degradation. Ecotones between ecosystems are touched upon by several different VLAs. Because conflicting terminology abounds in this area, we append a glossary defining the problematic terms used.     

基于生态系统服务的城市化区域生态风险表征方法研究

快速城市化导致城市周边区域生态系统服务损失并引发生态风险。以多种类型的生态系统服务作为生态风险的评价终点,构建了基于服务价值量的城市化区域生态风险表征方法,以北京市为例对方法进行了应用,并进行了风险评价结果的不确定性分析和参数敏感性分析。案例研究显示2015年北京市生态风险总体处于低风险接近中等风险水平,低风险和极低风险区域面积占全市的50%以上,主要分布于北京市西部和北部,高风险和极高风险区域面积占20%左右,主要分布于中心城区。生态风险空间格局特征表明北京市城市区域的扩张造成周边区域生态系统服务的下降,导致生态风险水平的上升。研究提出的生态风险指数同生态系统服务当量因子间具有显著的线性关系,可用于估算生态系统服务价值。不确定性和参数敏感性分析表明生态风险指数计算结果变异较小,指数具有较高的可靠性。研究方法能够综合表征城市化区域的生态风险,定量表征结果便于决策者理解,具有应用于风险评价和管理实践的价值。     

城市生态风险管理关键问题与研究进展

我国目前正处于社会经济转型和城市化进程加快时期,随着城市化发展和城市人居环境的变化,城市生态风险受到越来越多关注。在综述国内外城市生态风险管理研究进展,总结风险源与受体特点和风险评价方法的基础上,结合城市生态风险管理的需求,明确了城市生态风险的管理目标,将管理目标系统归纳划分为控制目标、调控目标和规划目标3个层次;在解析城市生态风险管理特点的基础上,结合风险管理目标从弹性力、动态管理性和空间异质性3个方面对生态风险管理措施与方案进行了总结分析,并进一步探讨了风险管理保障机制。从生态风险管理目标制定、构建城市生态系统特点的风险管理体系及其管理机制等方面提出了建议与展望,以期推动我国城市生态风险管理的发展。     

挠力河流域平原区湿地景观完整性评价

探讨一种景观完整性评价方法对湿地管理和保护非常重要.利用遥感和GIS技术,选择10个指标构建景观完整性指数,对挠力河流域平原区开展景观完整性评价.结果显示,1950年挠力河流域洪泛平原中的湿地景观完整性远好于2005年;人类活动影响越强的区域湿地景观完整性越差;2005年仅河岸带湿地景观比其它区域具有较好的景观完整性.由于景观完整性指数包涵了必要的景观结构和功能完整性特征信息,对评价景观尺度生态完整性,诊断生态受损区域,保护、恢复和管理湿地具有重要作用.     

基于时空分析的生态保护与修复试点工程实施效果评估——以赣州市为例

以“山水林田湖草生命共同体”为中心思想,从生态系统的格局和质量两个方面,对赣州市山水林田湖生态保护与修复试点工程实施效果进行了综合评估。结果如下：（1）从生态系统格局来看,2015到2018年,赣州市森林、农田和城镇生态系统面积明显增加,超过40%的草地生态系统转变为森林生态系统,且近45%的城镇生态系统面积增量由草地生态系统贡献。此外,多数自然生态系统的斑块破碎化加剧,森林生态系统破碎化现象最为明显,最大斑块指数从54.36降低到37.41,而半自然生态系统最大斑块指数增大。（2）从生态系统质量来看,赣州市归一化植被指数稳定在0.7以上并呈增长趋势,水土流失综合治理面积从16543.8 km²增长到18550.4 km²,重点流域水质基本稳定在Ⅱ、Ⅲ级,城镇生态系统受土壤重金属污染的风险较小,但部分县区农田生态系统受一种或多种土壤重金属污染的风险较大。整体而言,赣州市山水林田湖生态保护与修复试点工程取得了显著成效,较好的完成了实施方案中的规划目标。在进一步的生态保护与修复工作中,应重视赣州市自然生态系统斑块破碎化严重地区、水质出现波动较大的河流断面以及农田生态系统受土壤重金属污染威胁较大的县区。     

基于格局-过程生态适应性循环三维框架的自然景观生态风险评价——以黄土高原为例

传统的景观生态风险评估侧重于评价景观镶嵌体相对于最优格局的偏离程度,忽视生态系统过程和景观类型内部分异,使得黄土高原景观生态风险评估存在一定的片面性。综合"格局-过程"的生态适应性循环三维框架,构建适合自然生态系统的景观生态风险评价指标体系,对黄土高原2000年、2010年、2017年的景观生态风险进行评估。从空间分异来看,相较于传统的景观格局风险指数法仅在沙漠景观呈现高风险单一结果,本研究结果显示黄土高原景观生态风险由高到低依次为城市和沙漠景观、中部丘陵沟壑区草地景观、西北荒漠草地景观和东南部农田景观、东南部高山林地景观,具有明显空间分异。从时间变化来看,生态工程实施以来黄土高原景观生态风险总体呈现持续下降趋势,平均值由0.410降低到0.385,但2010-2017年下降不明显,生态工程持续实施对景观生态风险持续下降作用变弱。其中,自然景观（林地和草地）受生态工程促进生态风险持续降低,而人工景观（城市和农田）尤其是城市范围的不断扩大促使区域生态风险升高明显,建议加强城市土地集约高效利用,同时限制北部环境恶劣小城镇的发展。此外,中部丘陵沟壑区草地恢复力不足和降水侵蚀力增强也会促使风险升高,建议在生态保护时给予重点考虑。     

Regional Index of Ecological Integrity: A need for sustainable management of natural resources

An ecosystem is a complex composition of physical, chemical and biological components. This complex system remains in a healthy state if the system can maintain the ecological equilibrium among its components. Anthropogenic disturbances are the prime stressors that affect this equilibrium through creating fragmentation, ecosystem sensitivity, loosening landscape connectivity and disrupting ecological integrity. As different types of ecosystem are interconnected, a comprehensive monitoring and evaluating criteria is needed for measuring its integrity at regional level for conservation planning. A Regional Index of Ecological Integrity can be a suitable approach for sustainable management of regional ecosystem. Therefore, this paper presents (i) the characteristics of ecological integrity, (ii) the spatial processes induced by anthropogenic stressors and (iii) an approach to develop a composite Regional Index of Ecological Integrity (RIEI). The prime objective is to establish a thought and a way to develop a composite index of ecological integrity at the regional level. Here, we demonstrate different compositional, structural and functional indicators/indices related to fragmentation, representativeness of protected area, ecosystem sensitivity, and landscape connectivity for the development of a Regional Index of Ecological Integrity (RIEI).     

Restoration and management of riparian ecosystems: a catchment perspective

1. We propose that strategies for the management of riparian ecosystems should incorporate concepts of landscape ecology and contemporary principles of restoration and conservation. A detailed understanding of the temporal and spatial dynamics of the catchment landscape (e.g. changes in the connectivity and functions of channel, riparian and terrestrial components) is critical. 2. This perspective is based upon previous definitions of riparian ecosystems, consideration of functional attributes at different spatial scales and retrospective analyses of anthropogenic influences on river catchments. 3. Restoration strategies must derive from a concise definition of the processes to be restored and conserved, recognition of social values and commitments, quantification of ecological circumstances and the quality of background information and determination of alternatives. 4. The basic components of an effective restoration project include: clear objectives (ecological and physical), baseline data and historical information (e.g. the hydrogeomorphic setting and the disturbance regime), a project design that recognizes functional attributes of biotic refugia, a comparison of plans and outcomes with reference ecosystems; a commitment to long-term planning, implementation and monitoring and, finally, a willingness to learn from both successes and failures. 5. Particularly important is a thorough understanding of past natural disturbances and human-induced changes on riparian functions and attributes, obtained by a historical reconstruction of the catchment.     

Are ecosystems hormetic?

The phenomenon of hormesis has been observed mainly for the response of individual organisms to stress. A reasonable line of inquiry might explore the possibility of observing hormesis at other levels of ecological organization. This initial examination focuses on ecosystem hormesis. Explorations of hormetic responses of ecosystems to stress cannot be made independently of a fundamental concept of ecosystem. The scale‐dependence of ecosystem dynamics also influences whether an ecological disturbance is in reality a stressor. Ecosystem hormesis might be claimed if one or more components of an ecosystem exhibit hormesis. By this definition, ecosystem hormesis would be a trivial extension of hormesis observed for individual organisms. A non‐trivial extension of ecosystem hormesis would include the observation that integrated (i.e., holistic) measures of ecosystem structure or function displayed an hormetic response to an ecological stressor. Several such examples of ecosystem structural and functional hormesis are presented.     

Do introduced North American beavers Castor canadensis engineer differently in southern South America? An overview with implications for restoration

• 1 Twenty‐five pairs of North American beavers Castor canadensis Kuhl were introduced to Tierra del Fuego Island in 1946. The population has expanded across the archipelago, arriving at the Chilean mainland by the mid‐1990s. Densities range principally between 0.5–2.05 colonies/km. They have an impact on between 30–50% of stream length and occupy 2–15% of landscape area with impoundments and meadows. Beaver impacts constitute the largest landscape‐level alteration in subantarctic forests since the last ice age.
• 2 The colonization pattern, colony densities and impacted area indicate that habitat in the austral archipelago is optimal for beaver invasion, due to low predator pressure and suitable food resources. Nothofagus pumilio forests are particularly appropriate habitat, but a more recent invasion is occurring in adjacent steppe ecosystems. Nonetheless, Nothofagus reproductive strategies are not well adapted to sustain high beaver population levels.
• 3 Our assessment shows that at the patch‐scale in stream and riparian ecosystems, the direction and magnitude of exotic beaver impacts are predictable from expectations derived from North American studies, relating ecosystem engineering with underlying ecological mechanisms such as the relationships of habitat heterogeneity and productivity on species richness and ecosystem function.
• 4 Based on data from the species' native and exotic range, our ability to predict the effects of beavers is based on: (i) understanding the ecological relationships of its engineering effects on habitat, trophic dynamics and disturbance regimes, and (ii) having an adequate comprehension of the landscape context and natural history of the ecosystem being engineered.
• 5 We conclude that beaver eradication strategies and subsequent ecosystem restoration efforts, currently being considered in southern Chile and Argentina, should focus on the ecology of native ecosystems rather than the biology of this invasive species per se. Furthermore, given the nature of the subantarctic landscape, streams will probably respond to restoration efforts more quickly than riparian ecosystems.

     

Meta-ecosystems: a theoretical framework for a spatial ecosystem ecology

This contribution proposes the meta‐ecosystem concept as a natural extension of the metapopulation and metacommunity concepts. A meta‐ecosystem is defined as a set of ecosystems connected by spatial flows of energy, materials and organisms across ecosystem boundaries. This concept provides a powerful theoretical tool to understand the emergent properties that arise from spatial coupling of local ecosystems, such as global source–sink constraints, diversity–productivity patterns, stabilization of ecosystem processes and indirect interactions at landscape or regional scales. The meta‐ecosystem perspective thereby has the potential to integrate the perspectives of community and landscape ecology, to provide novel fundamental insights into the dynamics and functioning of ecosystems from local to global scales, and to increase our ability to predict the consequences of land‐use changes on biodiversity and the provision of ecosystem services to human societies.     

Freshwater as shared between society and ecosystems: from divided approaches to integrated challenges

The paper has its focus on water's key functions behind ecosystem dynamics and the water-related balancing involved in a catchment-based ecosystem approach. A conceptual framework is being developed to address fundamental trade-offs between humans and ecosystems. This is done by paying attention to society's unavoidable landscape modifications and their unavoidable ecological effects mediated by water processes. Because the coevolution of societal and environmental processes indicates resonance rather than a cause-effect relationship, humanity will have to learn to live with change while securing ecosystem resilience. In view of the partial incompatibility of the social imperative of the millennium goals and its environmental sustainability goal, human activities and ecosystems have to be orchestrated for compatibility. To this end a catchment-based approach has to be taken by integrating water, land use and ecosystems. It is being suggested that ecosystem protection has to be thought of in two scales: site-specific biotic landscape components to be protected for their social value, and a catchment-based ecosystem approach to secure sustainable supply of crucial ecosystem goods and services on which social and economic development depends.     

On the degradation of forest ecosystems by extreme events: Statistical Model Checking of a hybrid model

In this paper, we study the vulnerability of forest ecosystems perturbed by extreme events, such as those arising from climate change. To investigate the complex interactions between the biological dynamics of the forest and the climatic activity, we construct an original hybrid model, obtained by coupling a continuous reaction–diffusion system, which describes the spatio-temporal dynamics of the forest ecosystem, with a discrete probabilistic process, which models the possible occurrences of extreme events. Properties of ecological interest are considered: invariance of the persistence equilibrium, attraction to the extinction equilibrium and emergence of degraded states. Those properties of the hybrid model are verified through an extension of the Statistical Model Checking framework. We establish the existence of a threshold above which the persistence equilibrium of the forest ecosystem is compromised and give a numerical assessment of this threshold in terms of the probability and intensity of extreme events. We also present non-trivial parameter conditions for which the forest ecosystem converges to a degraded savanna-like state.