Proposed Definition of Environmental Damage Illustrated by the Cases of Genetically Modified Crops and Invasive Species

Abstract: The introduction of non‐native plant species and the release of genetically modified (GM) crops can induce environmental changes at gene to ecosystem levels. Regulatory frameworks such as the Convention on Biological Diversity or the EU Deliberate Release Directive aim to prevent environmental damage but do not define the term. Although ecologists and conservationists often refer to environmental effects of GM crops or invasive species as damage, most authors do not disclose their normative assumptions or explain why some environmental impacts are regarded as detrimental and others are not. Thus far, a concise definition of environmental damage is missing and is necessary for a transparent assessment of environmental effects or risks. Therefore, we suggest defining environmental damage as a significant adverse effect on a biotic or abiotic conservation resource (i.e., a biotic or abiotic natural resource that is protected by conservational or environmental legislation) that has an impact on the value of the conservation resource, the conservation resource as an ecosystem component, or the sustainable use of the conservation resource. This definition relies on three normative assumptions: only concrete effects on a conservation resource can be damages; only adverse effects that lead to a decrease in the value of the conservation resource can be damages; and only significant adverse effects constitute damage to a conservation resource. Applying this definition within the framework of environmental risk assessment requires further normative determinations, for example, selection of a threshold to distinguish between adverse and significant adverse effects and approaches for assessing the environmental value of conservation resources. Such determinations, however, are not part of the definition of environmental damage. Rather they are part of the definition's operationalization through assessment procedures, which must be grounded in a comprehensible definition of environmental damage.     

Transgenics and Vertebrate Cloning as Tools for Species Conservation

Abstract:  It has been suggested that transgenics and vertebrate cloning have a role to play in conservation. Now is the time to evaluate their risks and benefits, before these technologies are widely implemented in our field. Direct risks of transgenics include escape and introgression of transgenes into wild populations; weedy invasion by transgenic organisms; toxicity or pathogenicity of engineered organisms and their products; and human error in the field testing and tracking of transgenic organisms. Indirect risks include environmental effects of increased herbicide use; the danger that engineered organisms may aid the development of bioweapons; the likelihood that gene patenting will lead to the privatization of natural resources; and the diversion of support from less glamorous forms of conservation. Formal risk assessments are commonly used to evaluate transgenic procedures, but our incomplete understanding of both ecosystem processes and the action of transgenes renders most of these assessments scientifically and socially unjustified. Nevertheless, a few, low-risk applications of transgenics may be possible: for example, "super-sterile" ornamental cultivars. Vertebrate cloning poses little risk to the environment, but it can consume scarce conservation resources, and its chances of success in preserving species seem poor. To date, the conservation benefits of transgenics and vertebrate cloning remain entirely theoretical, but many of the risks are known and documented. Conservation biologists should devote their research and energies to the established methods of conservation, none of which require transgenics or vertebrate cloning.     

重金属对水生生物的生态毒理效应及生物耐受机制研究进展

近年来,随着国民经济的快速发展,重金属以其特有的性质而被大量的应用于生产生活当中,同时也由于各种原因造成了水体重金属污染现象。水体重金属污染不仅对水生生物的生长和繁殖造成了严重的威胁,同时也威胁到人类的健康。因此,重金属污染具有潜在的生态与健康风险。本文主要概括介绍了重金属对水生植物、动物、微生物的生态毒理效应以及水生生物对重金属的各种耐受机制,展望了重金属对水生生物生态毒理效应的未来研究重点和方向。     

应用物种敏感性分布评估多环芳烃对淡水生物的生态风险（Assessing Ecological Risks of Polycyclic Aromatic Hydrocarbons（PAHs）to Freshwater Organisms by Species Sensitivity Distributions）

阐述了利用物种敏感性分布进行生态风险评价的原理与方法,构建了淡水生物对8种常见多环芳烃(蒽、芘、苯并[a]芘、荧蒽、菲、芴、苊、萘)的物种敏感性分布;在此基础上,计算了这8种多环芳烃对不同类别生物的HC5(Hazardous Concentration for5%of the species)阈值,预测了不同浓度多环芳烃对生物的潜在影响比例PAF(Potentialaffected fraction),比较了不同类别生物对多环芳烃的敏感性,以及多环芳烃对淡水生物的生态风险,并对以红枫湖、黄河、白洋淀为代表的中国典型水体中的多环芳烃进行了联合生态风险评价.结果表明:1)当污染物浓度达到10μg·L-1时,半数多环芳烃的风险超过了5%的阈值;当浓度上升到100μg·L-1时,只有萘和苊没有显著生态风险.2)对于芴和荧蒽,无脊椎动物更为敏感;而对于萘,则脊椎动物更敏感.3)通过HC5值比较和SSD曲线图比较,可得出污染物对所有物种的生态风险大小依次为:蒽>芘>苯并[a]芘>荧蒽>菲>芴>苊>萘;对脊椎动物风险大小为:荧蒽>苊>萘;对无脊椎动物:蒽>芘>荧蒽>菲>芴>苊>萘.4)多环芳烃在红枫湖、黄河、小白洋淀的生态风险均较低,急性联合msPAF(multisubstance PAF)值小于1%.     

Limits of Concern: suggestions for the operationalisation of a concept to determine the relevance of adverse effects in the ERA of GMOs

Background

The European Food Safety Authority proposed a concept for the environmental risk assessment of genetically modified plants in the EU that is based on the definition of thresholds for the acceptability of potential adverse effects on the environment. This concept, called Limits of Concern (LoC), needs to be further refined to be implemented in the environmental risk assessment of genetically modified organisms.

Methods

We analyse and discuss how LoC can be defined for the environmental risk assessment for three different types of genetically modified plants. We outline protection goals relevant to the genetically modified plants in question and discuss existing concepts and suggestions for acceptability thresholds from the environmental risk assessment of different regulatory areas. We make specific recommendations for the setting and use of LoC for each type of genetically modified plant.

Results

The LoC concept can be suitably applied for the environmental risk assessment of genetically modified organisms, if the different protection goals in agro-environments are specifically considered. Not only biodiversity protection goals but also agricultural protection goals need to be addressed. The different ecosystem services provided by weeds inside and outside agricultural fields have to be considered for genetically modified herbicide-tolerant crops. Exposure-based LoCs are suggested based on knowledge about dose–effect relationships between maize pollen and non-target Lepidoptera for insect-resistant maize. Due to the long-term nature of biological processes such as spread and establishment, LoCs for genetically modified oilseed rape should be defined for the presence of the genetically modified plant or its genetically modified traits in relevant protection goals.

Conclusions

When setting LoCs, the focus should be on protection goals which are possibly affected. Potential overlaps of the LoC concept with the ecosystem service concept have to be clarified to harmonise protection levels in the agro-environment for different stressors. If additional impacts on agro-biodiversity resulting from the cultivation of genetically modified plants are to be avoided, then high protection levels and low thresholds for acceptable effects (i.e. LoC) should be set.

     

Incorporating Climate and Ocean Change into Extinction Risk Assessments for 82 Coral Species

Many marine invertebrate species facing potential extinction have uncertain taxonomies and poorly known demographic and ecological traits. Uncertainties are compounded when potential extinction drivers are climate and ocean changes whose effects on even widespread and abundant species are only partially understood. The U.S. Endangered Species Act mandates conservation management decisions founded on the extinction risk to species based on the best available science at the time of consideration—requiring prompt action rather than awaiting better information. We developed an expert‐opinion threat‐based approach that entails a structured voting system to assess extinction risk from climate and ocean changes and other threats to 82 coral species for which population status and threat response information was limited. Such methods are urgently needed because constrained budgets and manpower will continue to hinder the availability of desired data for many potentially vulnerable marine species. Significant species‐specific information gaps and uncertainties precluded quantitative assessments of habitat loss or population declines and necessitated increased reliance on demographic characteristics and threat vulnerabilities at genus or family levels. Adapting some methods (e.g., a structured voting system) used during other assessments and developing some new approaches (e.g., integrated assessment of threats and demographic characteristics), we rated the importance of threats contributing to coral extinction risk and assessed those threats against population status and trend information to evaluate each species’ extinction risk over the 21st century. This qualitative assessment resulted in a ranking with an uncertainty range for each species according to their estimated likelihood of extinction. We offer guidance on approaches for future biological extinction risk assessments, especially in cases of data‐limited species likely to be affected by global‐scale threats. Incorporación del Cambio Climático y Oceánico en Estudios de Riesgo de Extinción para 82 Especies de Coral     

A concise review of ecological risk assessment for urban ecosystem application associated with rapid urbanization processes

ABSTRACT

Urban ecological risk (UER) caused by rapid urbanization means potential threat to urban ecosystem structure, pattern and services. The scales of ecological risk assessment (ERA) have been expanded from individual organisms to watersheds and regions. The types of stressor range from chemical to physical, biological and natural events. However, the application of ERA in urban ecosystems is relatively new. Here, we summarize the progress of urban ERA and propose an explicit framework to illumine future ERA based on UER identification, analysis, characterization, modeling, projection and early warning and management. The summary includes six urban ERA-relevant methods: weight-of-evidence (WoE), procedure for ecological tiered assessment of risks (PETAR), relative risk model (RRM), multimedia, multi-pathway, multi-receptor risk assessment (3MRA), landscape analysis and ecological models. Furthermore, we review critical cases of urban ERA in landscape ecology, soil, air, water and solid waste. Based on the Internet of Things (IoT) and cloud computing, an urban ERA management platform integrates various urban ERA methodologies that can be developed to provide better implementation strategies of UER for urban ecosystem managers and stakeholders. We develop a conceptual model of urban ERA based on the urban characteristics in China. The future applications of urban ERA include uncertainty analysis using Monte Carlo techniques on the basis of geospatial techniques and comprehensive urban ERA using nonlinear models or process models.     

Scale Mismatches,Conservation Planning,and the Value of Social‐Network Analyses

Many of the challenges conservation professionals face can be framed as scale mismatches. The problem of scale mismatch occurs when the planning for and implementation of conservation actions is at a scale that does not reflect the scale of the conservation problem. The challenges in conservation planning related to scale mismatch include ecosystem or ecological process transcendence of governance boundaries; limited availability of fine‐resolution data; lack of operational capacity for implementation; lack of understanding of social‐ecological system components; threats to ecological diversity that operate at diverse spatial and temporal scales; mismatch between funding and the long‐term nature of ecological processes; rate of action implementation that does not reflect the rate of change of the ecological system; lack of appropriate indicators for monitoring activities; and occurrence of ecological change at scales smaller or larger than the scale of implementation or monitoring. Not recognizing and accounting for these challenges when planning for conservation can result in actions that do not address the multiscale nature of conservation problems and that do not achieve conservation objectives. Social networks link organizations and individuals across space and time and determine the scale of conservation actions; thus, an understanding of the social networks associated with conservation planning will help determine the potential for implementing conservation actions at the required scales. Social‐network analyses can be used to explore whether these networks constrain or enable key social processes and how multiple scales of action are linked. Results of network analyses can be used to mitigate scale mismatches in assessing, planning, implementing, and monitoring conservation projects. Discordancia de Escalas, Planificación de la Conservación y el Valor del Análisis de Redes Sociales     

转基因生物风险评估和管理的国家能力建设的探讨

转基因生物风险评估和管理的国家能力建设的内容,包括机构、机制、专家知识、环境监测以及信息收集和交流等。风险评估和管理的能力建设必须根据本国生物技术研究和应用水平、资金、信息以及人员数量和素质来确定其优先领域、行动和项目。目前,中国转基因生物风险评估和管理的国家能力建设工作亟待开展的有:成立国家生物安全委员会;建立转基因生物风险评估和管理的制度以及公众参与的机制;提高技术人员和管理者在生态学、遗传学和风险评估方法学等方面的专家技能;制定转基因生物的环境监测规划;建立有关转基因生物的环境监测网络和基地;新建一批生物安全数据库和信息库     

Entwicklung von ökotoxikologischen Instrumenten und ihre rechtliche Implementierung zur marinen ökologischen Risikobewertung von Chemikalien, Pestiziden und Baggergut

Background, aim, and scope The marine environment is often the final sink for pollutants, especially for persistent organic pollutants (POPs) and for persistent, bioaccumulative and toxic (PBT) substances. The body burden of marine top predators in the Baltic Sea, in the North Sea and also in the Arctic seas is alarming. Thus, the question was investigated if the European environmental law considers a prospective marine ecological risk assessment of chemicals, pesticides and dredged material before they are launched on the market or disposed to the sea. Results The analysis of European environmental law showed that the European environmental protection goals demand a good quality status of coastal waters until 2015 (Waterframework Directive) and a good quality status of European seas until 2020 (Marine Strategy Directive), but a specific marine ecological risk assessment of chemicals and pesticides is not sufficiently required in current European legislation. Discussion It was shown that the ecological risk assessment for freshwater ecosystems is, due to the pecularities of pollutant impacts in the marine environment, not adequate to predict marine effects and to protect the marine environment sufficiently. A statistical analysis of international databases on the relative toxicity of narcotics revealed that marine organisms can be significantly more sensitive than freshwater organisms towards substances with an unspecific mode of action (narcotics). Approximately 60?% of the industrial chemicals are classified as narcotics by their mode of action. Thus, this substance class is of environmental importance. Due to the hydrophobic properties and the low solubility of narcotics in seawater, the ecotoxicological assessment of marine sediments was of interest. An estuarine and marine bioassay test set was established and further developed to assess the ecotoxicological potential of brackish and seawater sediments. It was important that the test procedures were adapted to brackish and marine conditions and were harmonised between each other as well as on the international level. Conclusions Beside two bioassays for the ecotoxicological assessment of elutriates of marine and brackish sediments (bacteria bioluminescence test and marine algae test), the implementation and further development of the whole sediment bioassay with the marine amphipod Corophium volutator was important for enhancing the risk assessment. In order to gain a more standardised, all-season available test organism, the marine amphipod was for the first time reproduced under laboratory conditions the whole year round (also in winter), which is the essential basis for the urgently needed chronic whole sediment bioassay. The results of this investigation were implemented in the international (ISO), European (EN) and national (DIN) standardisations. Therefore, a standardised test set is ready for the implementation in the marine ecological risk assessment of chemicals, pesticides and dredged material in international, European and national legislation. Recommendations and perspectives Recommendations to improve the implementation of a marine risk assessment in European regulations are given with the goal to reach the internationally required objective of a sustainable development of the seas.     

Using expert knowledge to support Endangered Species Act decision-making for data-deficient species

Many questions relevant to conservation decision-making are characterized by extreme uncertainty due to lack of empirical data and complexity of the underlying ecologic processes, leading to a rapid increase in the use of structured protocols to elicit expert knowledge. Published ecologic applications often employ a modified Delphi method, where experts provide judgments anonymously and mathematical aggregation techniques are used to combine judgments. The Sheffield elicitation framework (SHELF) differs in its behavioral approach to synthesizing individual judgments into a fully specified probability distribution for an unknown quantity. We used the SHELF protocol remotely to assess extinction risk of three subterranean aquatic species that are being considered for listing under the U.S. Endangered Species Act. We provided experts an empirical threat assessment for each known locality over a video conference and recorded judgments on the probability of population persistence over four generations with online submission forms and R-shiny apps available through the SHELF package. Despite large uncertainty for all populations, there were key differences between species’ risk of extirpation based on spatial variation in dominant threats, local land use and management practices, and species’ microhabitat. The resulting probability distributions provided decision makers with a full picture of uncertainty that was consistent with the probabilistic nature of risk assessments. Discussion among experts during SHELF's behavioral aggregation stage clearly documented dominant threats (e.g., development, timber harvest, animal agriculture, and cave visitation) and their interactions with local cave geology and species’ habitat. Our virtual implementation of the SHELF protocol demonstrated the flexibility of the approach for conservation applications operating on budgets and time lines that can limit in-person meetings of geographically dispersed experts.     

Some Guiding Concepts for Conservation Biology

Abstract: The search for generalities in ecology has often been thwarted by contingency and ecological complexity that limit the development of predictive rules. We present a set of concepts that we believe succinctly expresses some of the fundamental ideas in conservation biology. (1) Successful conservation management requires explicit goals and objectives. (2) The overall goal of biodiversity management will usually be to maintain or restore biodiversity, not to maximize species richness. (3) A holistic approach is needed to solve conservation problems. (4) Diverse approaches to management can provide diverse environmental conditions and mitigate risk. (5) Using nature's template is important for guiding conservation management, but it is not a panacea. (6) Focusing on causes not symptoms enhances efficacy and efficiency of conservation actions. (7) Every species and ecosystem is unique, to some degree. (8) Threshold responses are important but not ubiquitous. (9) Multiple stressors often exert critical effects on species and ecosystems. (10) Human values are variable and dynamic and significantly shape conservation efforts. We believe most conservation biologists will broadly agree these concepts are important. That said, an important part of the maturation of conservation biology as a discipline is constructive debate about additional or alternative concepts to those we have proposed here. Therefore, we have established a web‐based, online process for further discussion of the concepts outlined in this paper and developing additional ones.     

多溴联苯醚、六溴环十二烷和四溴双酚A在环境中污染现状的研究进展

作为最主要的三大传统溴系阻燃剂(BFRs),多溴联苯醚(PBDEs)、六溴环十二烷(HBCD)、四溴双酚A(TBBPA)具有半挥发性、环境持久性和远距离传输性,目前在全球各种环境介质、生物体内广泛存在.毒理学研究表明,PBDEs、HBCD、TBBPA均具有明显的生物毒性和致癌性,对生态环境和人体健康存在潜在危害.本文简要概述了PBDEs、HBCD、TBBPA的使用现状,综述了全球范围内非生物体(灰尘、水体、土壤、沉积物、污泥)和生命体内(植物、动物、人体)等3种传统BFRs的污染水平、特征、暴露途径和毒性,并讨论了当前存在问题,最后对PBDEs、HBCD、TBBPA的未来研究进行了初步展望.     

Bewertung von Umweltwirkungen gentechnisch veränderter Organismen (GVO)

Genetically modified organisms (GMOs) can have effects on the environment in a variety of ways. The Genetic Engineering Act (Gen TG) stipulates that, before a GMO may be used, its characteristics have to be assessed and its behaviour in the environment has to be estimated and evaluated. The Federal Environmental Agency is the first and hitherto only authority involved in the implementation of the Genetic Engineering Act to have presented a risk assessment concept, in order to ensure that consent decisions taken in the enforcement of the Act are comprehensible and comparable. This concept is presented, as are proposals for the envisaged revision which results from changes in the legal framework, notably the adoption of the Biosafety Protocol, the Convention on Biological Diversity and the new EU Deliberate Release Directive 2001/18/EC. In addition, the contribution discusses the role of the precautionary principle and possible implications for decision-making by the authorities. The precautionary principle demands that environmental risks and damage should be avoided as far as possible, or prevented from arising at the outset. A particular challenge when refining assessment concepts is the integration of nature conservation principles. These have been given insufficient attention to date. The contribution presents the results of a workshop on this subject, which was jointly organised by the Federal Environmental Agency and the Federal Nature Conservation Agency. Those participating in the workshop identified aspects which go beyond the scope of the Genetic Engineering Act and are derivee from the specific objective of biotope and species protection. Furthermore, the contribution addresses the provisions of the new Deliberate Release Directive 2001/18/EC on environmental risk assessment (e.r.a.). The aim of e.r.a., on a case-by-case basis is, to identify and evaluate potential adverse effects of the GMO, either direct and indirect, immediate or delayed, on human health and the environment, which the deliberate release or the placement of GMOs on the market may have. There exists a link to the definition of goals for a sustainable agriculture which have to be considered when assessing the impact of GMOs.     

Climate change, agricultural insecticide exposure, and risk for freshwater communities

Climate change exerts direct effects on ecosystems but has additional indirect effects due to changes in agricultural practice. These include the increased use of pesticides, changes in the areas that are cultivated, and changes in the crops cultivated. It is well known that pesticides, and in particular insecticides, affect aquatic ecosystems adversely. To implement effective mitigation measures it is necessary to identify areas that are affected currently and those that will be affected in the future. As a consequence, we predicted potential exposure to insecticide (insecticide runoff potential, RP) under current conditions (1990) and under a model scenario of future climate and land use (2090) using a spatially explicit model on a continental scale, with a focus on Europe. Space-for-time substitution was used to predict future levels of insecticide application, intensity of agricultural land use, and cultivated crops. To assess the indirect effects of climate change, evaluation of the risk of insecticide exposure was based on a trait-based, climate-insensitive indicator system (SPEAR, SPEcies At Risk). To this end, RP and landscape characteristics that are relevant for the recovery of affected populations were combined to estimate the ecological risk (ER) of insecticides for freshwater communities. We predicted a strong increase in the application of, and aquatic exposure to, insecticides under the future scenario, especially in central and northern Europe. This, in turn, will result in a severe increase in ER in these regions. Hence, the proportion of stream sites adjacent to arable land that do not meet the requirements for good ecological status as defined by the EU Water Framework Directive will increase (from 33% to 39% for the EU-25 countries), in particular in the Scandinavian and Baltic countries (from 6% to 19%). Such spatially explicit mapping of risk enables the planning of adaptation and mitigation strategies including vegetated buffer strips and nonagricultural recolonization zones along streams.     

Lands for Long-Term Research in Conservation Biology

Abstract: Success in conservation biology depends upon a synergistic combination of short-term tactics and long-term strategies. Although the former are often necessary to forestall immediate habitat losses, the latter provide the critical framework of understanding needed to develop effective short-term priorities. Although many conservation biologists now emphasize short-term tactics, prudence dictates the concomitant establishment of long-term research projects aimed at answering fundamental ecological questions.
One deterrent to amassing such long-term data bases, aside from time and funding, is a lack of suitable sites where such studies can be conducted on a large scale. We describe two established major land-holding networks in the United States that could serve as appropriate places to develop long-term studies: the National Science Foundation's Long-Term Ecological Research (LTER) sites, and the US. Department of Energy's National Environmental Research Parks (NERPs). Because they consist of established research facilities, both networks can provide conservation biologists with "low-cost" baseline information on ecological processes, as well as access to a number of representative terrestrial and aquatic habitats under more or less "controlled" conditions suitable for long-term studies. We recommend that conservation biologists explore the possibility of using these or similarly available sites in their research programs.     

农药对陆生生物的生态毒性及风险评估

农药的使用会对非靶标生物造成影响,由此世界各国都采取了风险控制手段以预防农药造成的生态危害。本文综述了欧洲、美国和日本针对农药开展的陆生生态系统风险评估方法,包括陆生非靶标生物、风险评估模型、风险评估的基本方法及生态毒性的评价指标。同时分析了农药登记管理对陆生生生物的生态毒性及风险评估中存在的科学问题,且提出了方法学的发展方向。     

Chemical speciation and potential ecological risk assessment of heavy metals in volcanic rocks of Southern Qinghai,China

ABSTRACT

Seven volcanic rocks samples were collected from Southern Qinghai to analyze chemical speciation and migration behavior of heavy metals by sequential chemical extraction procedure and column leaching test. The geo-accumulation index, ecological risk index and the risk assessment code were applied to assess the heavy metal pollution and potential environmental effects in this area. Results revealed that the total concentrations of heavy metals did not exceed the background values in soil of this area. Most of the samples produced acid rock drainage. The order of heavy metal migration and transformation sequence in the volcanic rocks of Zhiduo region was Cd?>?Pb?>?As?=?Cu?=?Zn?=?Mn based on the geo-accumulation index and Cd caused heavy pollution, which was also confirmed by the leaching test. Moderate potential ecological risk posed by heavy metals occurred in the study area based on the potential ecological risk index. Cd contributed to most of ecological risk while the remaining heavy metals (except As) exerted medium to high risks to the environment according to the risk assessment code evaluation results. In summary, volcanic rocks possessed potential risks to the surroundings due to potential release of heavy metals. Cd that caused the pollution should be paid special attention.     

水体和沉积物中毒害污染物的生态风险评价方法体系研究进展

人类活动导致大量毒害污染物进入水体和沉积物,从而对水生生物产生诸多不利影响.开展毒害污染物的生态风险评价,筛选高风险毒害污染物,是毒害污染物风险管控和生态系统保护的基础.对美国和欧盟等发达国家和地区毒害污染物的生态风险评价方法进行了综述.水体和沉积物中毒害污染物风险评价的基本方法首先是采用预测或测定环境浓度(PEC或M...