EuropeanStrategyonInvasiveAlienSpecies英
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如何抵御物种入侵英语作文
如何抵御物种入侵英语作文英文:Invasive species are a major threat to ecosystems around the world. These species, which are not native to a particular area, can cause significant damage to the environment, economy, and even human health. As a result, it is important to take steps to defend against invasive species.One way to defend against invasive species is through prevention. This can be done by implementing strict regulations on the import and export of goods, such as plants and animals, which can carry invasive species. For example, in the United States, the Department ofAgriculture has strict regulations on the importation of plants and plant products to prevent the spread of invasive species.Another way to defend against invasive species isthrough early detection and rapid response. This involves monitoring and identifying potential invasive speciesbefore they become established and cause harm. For instance, in Australia, the government has established a network of volunteers who help to monitor and report on the presenceof invasive species in their local areas.In addition, controlling and managing invasive speciesis crucial in defending against their spread. This can involve methods such as mechanical removal, chemical control, and biological control. For example, in New Zealand, the government has implemented a program tocontrol the spread of invasive plants by using biological control agents, such as insects, to reduce their populations.Overall, defending against invasive species requires a combination of prevention, early detection, and effective management strategies. By taking these steps, we can helpto protect our ecosystems and prevent the negative impactsof invasive species.中文:入侵物种对世界各地的生态系统构成了重大威胁。
The contribution of
The contribution of Environmental Impact Assessment (EIA)to decision making for biological pest control in South Africa –The case of Lantana camaraL.A.Sandham *,T.H.Carroll,F.P.RetiefEnvironmental Assessment Research Group,School of Environmental Sciences,North-West University,Private Bag X6001,Potchefstroom,South Africaa r t i c l e i n f o Article history:Received 22April 2009Accepted 10December 2009Available online 16December 2009Keywords:Environmental Impact Assessment (EIA)Environmental Impact Assessment report qualityBiological control Decision making Lantana camaraa b s t r a c tIn many countries authorization for the release of biological control agents for invasive species such as Lantana camara requires the consideration and evaluation of environmental impact and risk assessment reports.In South Africa the release of biocontrol agents is subject mainly to Environmental Impact Assessment,in terms of which various agents have been authorized for release into the environment for the control of L.camara .However the quality of the EIA reports that form the basis for decision making has not been evaluated.An EIA review package adapted to the requirements of biological control agents was used to review the quality of six approved EIA reports to gauge the contribution of EIA to decision making on the release of these biological control agents.The main finding is that the quality of the reports is poor measured against international best practice.The main weaknesses relate to the crux of EIA which is impact identification,impact evaluation,scoping,mitigation measures and monitoring programs.The value of EIA as a tool for Integrated Environmental Management of complex and potentially high impact activities such as the release of biological control agents is found to be less than required.Ó2009Elsevier Inc.All rights reserved.1.Introduction1.1.Biological pest control –the role of EIAInvasive alien species are recognized as one of the greatest bio-logical threats to the planet’s environmental and economic well being (McNeely et al.,2001)and include most detrimental pests,crop diseases and invasive weeds.Consequently,nations are grap-pling with complex and costly invasive species problems.It is therefore of vital importance to implement stringent tests and con-trols to ensure that biological control agents are effective,host spe-cific and that the species used for biological control do not in turn become problematic,e.g.have adverse impacts on non-target spe-cies (McNeely et al.,2001).In this regard,methods such as risk analysis and Environmental Impact Assessment (EIA)have been widely used internationally as pro-active decision support tools to avoid or minimize the potential impact associated with the introduction of biological pest control agents (Arnett and Louda,2002;Baars et al.,2003;Sheppard et al.,2003,2005;Berner and Bruckart,2005;Briese,2005;Louda et al.,2005;Wright et al.,2005;Ding et al.,2006;Hunt et al.,2008).South Africa is classified among the world leaders in the field of biological control of invasive plants (Klein,2002;Zalucki et al.,2007).Since 1914,the Agricultural Research Council’s Plant Protec-tion Research Institute and its predecessors have released more than 80species of biological control agents,to control 35invasive alien plant species.According to Klein (2002)remarkable successes have been achieved with either controlling or reducing the inva-sive potential of many invasive alien plants.However,notwith-standing these successes,invading alien plants have become established in over 10million hectares of land (http://www.dwaf.-gov.za/wfw/)and the cost of controlling them is estimated at R600million per year (Approx $80million in 2009).The eradication and control of invasive alien species therefore requires the implemen-tation of integrated pest management strategies of which biologi-cal control is one component (Hoffmann and Frodsham,1993).It is therefore imperative that the environmental and economic risks of introducing an alien control agent need to be considered,prior to release,in the context of the risks posed by the alien invader should no control be imposed.Such risks and considerations have been incorporated into a range of protocols by various countries where biological control agents are used.Risk analysis is the principal instrument used by regulatory bodies in Australia,Canada,New Zealand and the US for authorization of the import and release of BCAs (Sheppard et al.,2003;Hunt et al.,2008).In terms of environmental legisla-tion,EIA forms part of the process in Australia and the United States.By contrast,in South Africa,two independent processes are required for authorization.The first process is mandated by the1049-9644/$-see front matter Ó2009Elsevier Inc.All rights reserved.*Corresponding author.Fax:+2786622152.E-mail addresses:luke.sandham@nwu.ac.za ,luke.sandham@ (L.A.Sandham).Agricultural Pest Act and the Conservation of Agricultural Re-sources Act(Anon.,1983a,b),in terms of which the Directorate for Plant Health of the Department of Agriculture,Forestry and Fisheries(formerly the Department of Agriculture)requires that host-specificity tests,including some components of risk assess-ment,be conducted before an application for release of a BCA is ap-proved.The majority of tests are conducted by the Plant Protection Research Institute of the Agricultural Research Council.The tests are paid for by the client,usually a government agency such as the‘‘Working for Water”program,whose aim is to remove water-intensive alien invaders.The application,supported by the results of the host-specificity tests,is then submitted to the Direc-torate of Plant Health,who refers it to the Biological Control Re-view Panel,consisting of a number of experts in biological control.The application is reviewed independently by at least three members of a panel,who submit their reviews and recom-mendations to the Department of Agriculture,Forestry and Fisher-ies,where a decision is made either to authorize release of the agent,or to refer it back for more research.The second process for authorization of the release of an agent is the EIA,mandated since1997in terms of the Environment Con-servation Act(Anon.,1989)and since2006in terms of the National Environmental Management Act(Anon.,1998).This is a separate authorization for the release of a biocontrol agent,based on Envi-ronmental Impact Assessment alone.This is a highly formalized process with extensive public participation,and authorization can only be issued after consideration of reports concerning the impact on the environment of the agent and of alternatives to the agent(Anon.,1989,1997a,b,1998,2006a,b).In this regard, the EIA report is a major component of decision making on autho-rizations for the release of BCAs in South Africa.While the host-specificity tests conducted for the DAFF authorization are included in the EIA reports,the EIA is conducted as a completely separate process,with a wider focus on environmental impacts,influenced by the very wide definition given to the environment in the Na-tional Environmental Management Act(Anon.,1998).This has led to some frustration in the biological control community,where release of BCA has long been dealt with as mainly an agricultural–ecological issue,and where the precautionary risk-averse approach now embodied in the EIA process is seen as unnecessarily delaying and complicating the task of biological control(Sheppard et al., 2003;Urban A.,personal communication,2009).Given the important role of EIA for biological control in South Africa,and its supporting role in other countries and contexts regarding the use of EIA for introduction of biological control agents,its effectiveness has not been well researched and there is consequently a dearth of peer-reviewed literature on this theme. The aim of this paper is therefore not an international comparative study of BCA per se,but an investigation of the efficacy of the South African experience of using EIA for authorization of BCA release, with particular focus on EIA report quality.It is beyond the remit of this paper to investigate the merits of the South African govern-ment’s approach to the release of biocontrol agents.1.2.The Lantana camara challengeLantana camara(lantana)L.is afloriferous,prickly,thicket-forming hybrid shrub of tropical and sub-tropical South and Central American origin(Zalucki et al.,2007).It is an aggressive, vigorously growing weed that tolerates a wide variety of environ-mental conditions(Baars and Neser,1999).L.camara has the inva-sive status of a‘‘transformer”,indicating its ability as a mono-species to dominate or replace any canopy or sub-canopy layer of a natural or semi-natural ecosystem,thereby altering its structure, integrity and functioning(Henderson,2001).The most serious is rated as one of the world’s worst weeds(Baars and Neser, 1999;Zalucki et al.,2007).It out-competes indigenous vegetation by preventing the regeneration of indigenous vegetation through the secretion of allelopathic chemicals(Gentle and Duggin,1997).As an alternative or supplement to chemical and mechanical control methods,biological control is considered as a cost-effec-tive,environmentally benign,long-term solution(Hunt et al., 2008).However,despite the biological control program against lantana being the largest and longest running biological weed con-trol program in the world,with a total of41biological control agents released worldwide since1902,it has thus far met with lim-ited success(Baars and Neser,1999;Sheppard,2003;Zalucki et al., 2007).The lack of success has been attributed to a number of factors including inadequate understanding of the taxonomy of the plants, poor climate matching,and the genetic diversity of lantana,which has made it an extremely variable target weed,presenting the bio-logical control agents with several morphological and physiologi-cal barriers to utilization(Baars and Neser,1999;Zalucki et al., 2007).The success of the biological control program for lantana de-pends on the establishment of a suite of control agents,attacking several parts of the weed and which are able to cope with extreme variability and wide distribution(Baars and Neser,1999).In South Africa lantana is listed as a‘‘declared weed”in terms of the Conservation of Agricultural Resources Act(CARA)(Anon., 1983b).Specific provisions in terms of CARA aim to combat and control weeds such as lantana.Despite the large number of natural enemies that have been established on lantana since the1960s,it still remains one of the most vigorously growing,invasive weed species in South Africa(Klein,2002).Van Wilgen et al.(2004)cal-culated the potential area that is suitable for invasion by lantana in South Africa at44,663km2.By the year2000,despite ongoing con-trol measures,lantana had already invaded18,414km2(41.3%)of its potential range.1.3.The relevance of EIA report qualityIt is widely recognized that a well functioning EIA system should include a systematic review of the quality of the EIA report (EIR),which functions as one of the main‘‘checks and balances”built into the EIA process(UNEP,2002:349).The review of EIA re-port quality assists the authorities by providing them with a tool to verify that the information in the report is credible and sufficient for decision-making purposes.Additionally,it imparts public con-fidence in the EIA process.The evaluation of the quality of EIA re-ports by means of review packages is one of a range of methods that can be used to assess the quality and adequacy of EIA reports (UNEP,2002:358)and to this end,various review packages and guidelines have been developed(European Commission,1994; Lee,2000;Wood,2003;).A key strength of review package design is to allow generic comparison of quality across the range of activ-ities requiring EIA,without being influenced by the unique aspects of individual projects.Report quality review has been widely and successfully applied to assess the status and standard of project-level EIA for a wide range of activities that which may give rise to significant environ-mental impacts(Lee et al.,1999).The Lee and Colley package is well-known and widely applied in developed and developing countries and has been widely used in the UK and in a number of other countries,including Belgium,Denmark,Germany,Greece, Ireland,Portugal,Spain and South Africa(Glasson et al.,2005; Rzeszot,1999;Lee,2000;Sandham et al.,2008b).However,review packages are used mainly in a research context,and do not appear to be routinely used by decision-making agencies.The review of the quality of EIA reports has lead to the realization that in spite142L.A.Sandham et al./Biological Control55(2010)141–149the quality of EIA reports is highly variable(Glasson,1996;Asian Development Bank,1997;Barker and Wood,1999;Morrison-Saun-ders et al.,2001;Simpson,2001;Bankwatch,2003;Almansa et al., 2005).Most EIA reports contain sound theoretical bases and thorough descriptions of the proposed projects,but the scientific and techni-cal information that determines the levels and significance of po-tential adverse impacts and which forms the basis for decision making is often inadequate.The reasons for the poor quality of EIA reports are mainly unqualified and/or inexperienced environ-mental assessment practitioners,insufficient time andfinances to obtain the relevant and adequate information,inadequate terms of reference or plan of study for the EIA undertaken,and deci-sion-making authorities that do not enforce continual improve-ment(Asian Development Bank,1997;Barker and Wood,1999; Morrison-Saunders et al.,2001;Simpson,2001;Bankwatch, 2003;Almansa et al.,2005).It is clear that information on establishment,spread and target impacts should be included in an EIA report for the release of the biological control agent.These issues influence the success of the biological control agent after release into the environment and should therefore be investigated,addressed and reflected in EIA re-ports to facilitate informed and responsible decision making.Much of this information is also required in the risk assessments con-ducted prior to release of BCAs in Australia,New Zealand,Canada and the US(Sheppard et al.,2003;Hunt et al.,2008).While EIA report quality has been investigated for various sec-tors in South Africa(Sandham and Pretorius,2008;Sandham et al., 2008a,b;Van der Vyver,2008)no investigation has been done for biological control agents.Since1997seven EIA reports(EIRs)for the release of biological control agents for lantana have been sub-mitted to and approved by the Department of Water and Environ-mental Affairs(DWEA,formerly the Department of Environmental Affairs and Tourism–DEAT).The main aim of this research is to evaluate the quality of EIA reports on biological control of lantana, with a view to provide decision support and guidelines for future decision making,and to serve as a baseline of EIR quality against which future EIAs can be measured.2.Materials and methodsThe Lee and Colley review package(Lee and Colley,1992;Lee et al.,1999)consists of multiple criteria arranged in a four-level hierarchical structure consisting of an overall report level,four re-view areas,17categories and55sub-categories,which are used to assess the quality of environmental impact reports,using assess-ment scores.The quality review evaluates how well a number of assessment tasks(sub-categories,categories and areas)have been performed.The review commences at the lowest level(sub-catego-ries)with the evaluation of simple criteria relating to specific tasks and procedures,and a qualitative,nominal score ranging from A to F(Table1)is awarded to each sub-category.The assignment of scores is subjective,but it is guided by supportive prompts,which are not strictly points to check off,but do allow for a reasoned assignment of a score on the nominal scale.An example of review sub-category1.1.1serves as illustration:1.1.1.The biological control agent proposed for release should bedescribed.This should include the following:taxonomic informa-tion,identification of the species(characteristics),method of repro-duction,distribution of species and mobility of the species.The extent of compliance to the issues suggested by the prompts,guides the reviewer in evaluating the degree of‘‘satisfac-toriness”or lack thereof,and in assigning a score.For example,in the case of sub-category1.1.1,if the EIR contained only a descrip-tion of the distribution of the species and nothing else suggested by the prompts,it would not be satisfactory,and it would be as-signed a score of E or F,depending on the comprehensiveness of the description of the distribution.The reviewer moves progressively to the higher levels in the hierarchy,applying more complex criteria to broader tasks and procedures in the process,and assigning a score to each category and review area until the overall assessment of the EIR has been completed with an overall score for the report as a whole.A sche-matic presentation is provided in Fig.1.Nominal scores ranging from A to F(Table1)are used in prefer-ence to numbers,in order to avoid crude aggregation or arithmet-ical averaging,which can distort results which are essentially qualitative(Lee et al.,1999;Simpson,2001).Since a criterion can only be assessed as essentially satisfactory(A,B or C)or unsatisfac-tory(D,E or F)no‘‘average”score can be allocated.The critical boundary is therefore between C and D scores.The assessment scores are recorded on a Collation Sheet.Whereas EIA practice is shaped by the regulatory system,cur-rent EIA practice in South Africa is intended to emulate interna-tional best practice.The intent of the review package is to evaluate performance against international best practice,and therefore,if a report performs poorly,it indicates sub-standard practice.Poor performance in aspects NOT required by the South African EIA system therefore indicts the EIA system,and in this way,the review of EIA report quality constitutes an indirect evalu-ation of the EIA system as a whole.However,due to various capac-ity constraints,the use of review packages to assess the quality EIA reports is not standard practice among environmental authorities in South Africa,although recent and current research on report quality might encourage such practice.The Lee and Colley package has been modified in various in-stances in order to address sector-and context-specific require-ments(Lee,2000;Simpson,2001).Except for general criteria relating to the communication of information,consideration of mitigation measures and alternatives,the criteria for the evalua-tion of EIRs on the release of biological control agents need to be appropriately different from the criteria used in the standard Lee and Colley review package,in terms of specialist information on biological control and existing guidelines.In this case,it was modified by the authors in line with South African requirements and understanding of BC.The authors recog-nize the existence of various other international protocols andTable1List of assessment scores.Score ExplanationA Relevant tasks well performed,no important tasks left incompleteB Generally satisfactory and complete,only minor omissions and inadequaciesC Can be considered just satisfactory despite omissions and/or inadequaciesD Parts are well attempted but must,as a whole,be considered just unsatisfactory because of omissions or inadequaciesE Not satisfactory,significant omissions or inadequaciesF Very unsatisfactory,important task(s)poorly done or not attemptedL.A.Sandham et al./Biological Control55(2010)141–149143requirements,such as the TAG manual (USDA,2000)used in the USA.These were however not included in the revised review crite-ria,in order to ensure that the evaluation is valid for country and activity specific requirements and conditions.Apart from relatively small reductions in the number of review categories and sub-cate-gories,the structure,number of review areas and the assessment scores of the original review package remained essentially un-changed.The reductions were due mainly to the difference be-tween the development approach reflected in the EIA regulations,and the ‘‘restoration”approach of biological control.Issues such as the description and size of the site,and the duration of the phases of the development,were deemed inappropriate and left out.Moreover,the wording of the review questions,particularly in Review Area 1,was changed to appropriately reflect biological control rather than development projects.The adapted package therefore accommodates modifications specific to the activity,but retains sufficient generic structure to allow for comparison of EIR quality from other activities as well as other countries.An abbreviated version of the review areas,categories and sub-catego-ries,as adapted for the review of EIRs of biological control agents,appears in Table 2.The full review package is included in Carroll (2006)and in Appendix A (Online version only).The EIA reports for six biological control agents introduced for L.camara were reviewed using the modified version of the package (Table 3).The control agents were all released between 1998and 2006,and the EIAs were all conducted in terms of the same EIA regulatory procedure,with no significant difference in information required.No evidence could be found of any peer-reviewed litera-ture dealing with report quality of EIA reports for BCA in any other country.Hence,the quality review of these EIA reports constitutes the first time that the Lee and Colley review package has been used for EIAs for BCA applications.The reviews were conducted in accordance with the standard procedure for the use of the Lee and Colley review package (Lee et al.,1999),as described at the beginning of this section.A more detailed description of the procedure appears in Lee et al.(1999).3.Analysis,results and discussionAs shown above,the quality review criteria are arranged in a hierarchical structure consisting of an overall report grade,review areas,categories and sub-categories.Lower levels therefore inform the quality review scores at higher levels.The analysis and inter-pretation of results reflected in the following sections starts by pre-senting the overall report grade and then grades the expanded hierarchy of different review areas,categories and sub-categories.The discussion therefore develops from a more general and holisticFig.1.The hierarchical structure of the Lee and Colley review package (Lee et al.,1999).Table 2Adapted EIR quality review criteria.1.Description of the biological control agent 1.1.Description of the biological control agent 1.1.1.Description of biological control agent1.1.2.Description of origin of biological control agent 1.1.3.Full scope of target plants described1.1.4.Description of damage by agent to target plant 1.1.5.Prior release information1.1.6.Number and frequency of agents to be released1.2.Receiving environment description1.2.1.Area and location/s for release described and mapped1.2.2.Proximity of potential non-target indigenous species should be indicated on maps1.2.3.Description of surrounding land uses1.2.4.Potential spread of species from release sites indicated and mapped 1.3.The proposed target invasive alien plant species/pests1.3.1.Description of target species including:taxonomy,species,reproduction,invasive status and distribution1.3.2.Current/projected status within next five years,with and without biological control agent1.3.3.Impact of target species on South Africa’s biodiversity1.3.4.Provide details of other biological control agents released for the control of the target species2.Identification and evaluation of key impacts 2.1.Definition and identification of impacts2.1.1.Description of all effects of agent on environment 2.1.2.Description of interaction of effects2.1.3.Impacts from non-standard operating procedure 2.1.4.Systematic methodology for impact identification2.2.Scoping:Key impacts identifiedrmation on public participation process 2.2.2.Key impacts identified for further investigation2.2.3.Impact areas not selected for thorough study should be identified and reasons given 2.3.Prediction of impact extent and intensity2.3.1.Data for impact magnitude estimation given 2.3.2.Methodology of impact magnitude predictions 2.3.3.Prediction of impact magnitude quantified 2.4.Assessment of impact significance2.4.1.Significance of impact w.r.t.standards 2.4.2.Significance of impact after mitigation2.4.3.Justify standards and values for significance 3.Alternatives and mitigation 3.1.Feasible alternatives3.1.1.Alternative methods should be considered 3.1.2.Discussion and reasons for final choice 3.1.3.Investigation of no go alternative3.2.Scope &effectiveness of mitigation measures 3.2.1.Mitigation of significant impacts considered3.2.2.Mitigation to include measures if agent becomes invasive or detrimentalsummary of the quality performance results for the report overall as well as the review areas.3.1.Overall report qualityThe quality review results(Table4)reveal that the overall re-port quality is poor,with four EIRs(Cases3–6)evaluated as‘just unsatisfactory’(D)and the remaining two EIA reports(Cases1 and2)as‘very unsatisfactory’(F)and‘not satisfactory’(E).Two broad patterns are evident in the review areas.Firstly,Re-view Areas2and3representing the more technical requirements relating to impact identification,consideration of alternatives,mit-igation measures and monitoring,are the areas with the most weaknesses and the poorest performance.Secondly,Review Areas 1and4,relating to the descriptive and presentational elements of the EIR,have a generally better performance.These patterns are in agreement with EIR qualityfindings inter-nationally and in South Africa specifically,although the relative score ratings are significantly lower for the biological control EIRs (Barker and Wood,1999;Lee,2000;Simpson,2001;Bankwatch, 2003;Sandham and Pretorius,2008;Sandham et al.,2008a,b). The general explanation is that descriptive aspects are easier to deal with than technical and methodological problems.Although the review package does not make provision for relative weighting of scores across review areas,it could be argued that Review Areas 2and3are the most important inputs to an EIR,and represent the essence of EIA.However,to gain a more detailed understanding the following sections focus on distilling the specific weaknesses as re-flected by the category and sub-category scores per review area.3.2.Quality of review areas3.2.1.Quality of Review Area1–Description of the biological control agentReview Area1provides the background information about the activity and the reasons for the proposed release of the biological control agent.The analysis of the categories and sub-categories of Review Area1appears in Table5.Category1.1(description of the control agent)was evaluated as just satisfactory(C)for Cases1,2,5and6and as generally satisfac-tory(B)for Cases3and4,due to satisfactory provision of adequate mation relating to taxonomy,origin of the species,damage caused by the proposed biological control agent and previous releases.In three of the reports(Cases2,5and6),no indication was given whether prior releases took place or not(sub-category1.1.5).Such information can assist authorities in making an optimal decision, as shown by retrospective studies(Louda et al.,2005)emphasizing the benefit of assessing the direct and indirect effects of a biologi-cal control agent that has been released into the environment.Sub-category1.1.6(the number and frequency of control agents to be released)was evaluated as very unsatisfactory(F)for all the EIRs,due the absence of such information.It was not clear whether the applicant/consultant did not consider it as important informa-tion or whether it had not been determined and therefore not in-cluded in the report.Taking into consideration the importance of the establishment and proliferation of the biological control agent in determining its efficacy(McFadyen,2003;Louda et al.,2005), the omission of this information is a major deficiency in the report.The description of the receiving environment(category1.2)was unsatisfactory for all cases(3Fs and3Ds),following from the poor performance in the sub-categories.Only sub-category 1.2.1 (description of area proposed for release)was evaluated as satis-factory(B)for Cases4,5and6,with maps and some general infor-mation on where the proposed agent will be released,while the other three EIRs were evaluated as not satisfactory(E)and very unsatisfactory(F)because of a lack of such information.Sub-categories1.2.2(proximity of potential non-target indige-nous species which were utilized by biological control agent during host-specificity tests),1.2.3(land uses of surrounding areas)and 1.2.4(potential spread of species from the release sites)were eval-uated as very unsatisfactory(F)throughout,with a single E in sub-category1.2.2.These poor results are mainly due to the absence of information regarding these issues.The poor performance is of concern since the results of the host-specificity testing indicated an indigenous Lippia species was utilized.According to the EIRs the degree of utilization and damage to the Lippia species was min-imal compared to that of its natural host,lantana,and the Lippia species are highly unlikely to sustain populations of biological con-trol agents in thefield over time.The EIRs state that the control agents utilize the Lippia species most likely because the Lippia spe-cies and lantana have at least one secondary chemical in common.The release of the proposed control agents was justified by stat-ing in at least three of the EIRs(Cases4,5and6)that the degree of possible suppression of Lippia species by the biological control agents is far less than the threat that is posed by the target species (lantana)invading the natural habitat of these indigenous species. While the negative impact of lantana on the environment justifies the use of biological agents as a control option,the multiple release thus far of control agents causes concerns regarding their cumula-tive impacts on non-target indigenous species,such as the Lippia species.Information on the target species(sub-category1.3)in the EIRs for Cases1,4,5and6was evaluated as satisfactory(B and C),due to adequate information relating to the target species,its status and distribution(sub-categories1.3.1and1.3.2),its impact on bio-diversity and economy(sub-category1.3.3)and other biologicalTable2(continued)mitment to mitigation3.3.1.Record of commitment to mitigation measures3.3.2.Monitoring programmes for impacts and provision to adjustmitigationmunication of resultsyout4.1.1.Introduction briefly describing the project4.1.2.Logical arrangement of information4.1.3.Chapter summaries4.1.4.External sources acknowledged4.2.Presentation:Accessible to non-specialistprehensible to non-specialist4.2.2.Glossary for technical terms,acronyms,etc.4.2.3.Presented as an integrated whole4.3.Emphasis4.3.1.Emphasis given to severe impacts4.3.2.EIR should be unbiased4.4.Non-technical summary4.4.1.Non-technical summary,incl.technical terms4.4.2.Summary to cover main issues1.Review area;1.1.Review category;1.1.1.Review sub-category.Table3Summary of selected sample reports.Case1Falconia intermedia(Mirid bug)Case2Mycovellosiella lantanae ntanae(leaf spot fungus) Case3Ophiomyia camarae(herringbone leaf-miningfly)Case4Coelocephalapion camarae(lantana petiole weevil) Case5Leptostales ignifera(Mexican leaf-feeding inch-worm) Case6Longitarsus bethae(root-feedingflea beetle)For the rest of the paper,the reports will be referred to by the case number.L.A.Sandham et al./Biological Control55(2010)141–149145。
介绍外来物种入侵的作文
介绍外来物种入侵的作文英文回答:Invasive species, also known as alien species or exotic species, refer to plants, animals, or microorganisms that are not native to a specific ecosystem and have the potential to cause harm to the environment, economy, or human health. The introduction of invasive species can occur through various means, such as accidental transportation, intentional release, or natural dispersal.One of the main reasons why invasive species pose a threat is their ability to outcompete native species for resources. They often have no natural predators or diseases in their new habitat, allowing them to reproduce rapidly and dominate the ecosystem. This can result in the decline or even extinction of native species, disrupting the balance of the ecosystem.For example, the introduction of the Asian carp intothe Great Lakes of North America has had devastatingeffects on the native fish populations. These carp are voracious eaters and can quickly deplete the food resources that native fish rely on. As a result, the native fish populations have declined significantly, leading to economic losses for the fishing industry and negative impacts on the overall ecosystem.Invasive species can also have economic impacts. They can damage crops, forests, and infrastructure, leading to financial losses for industries and governments. For instance, the emerald ash borer, a beetle native to Asia, has caused extensive damage to ash trees in North America. The cost of treating or removing infected trees, as well as the loss of timber and aesthetic value, has had a significant economic impact on affected regions.Furthermore, invasive species can pose risks to human health. Some species may carry diseases or parasites that can be transmitted to humans or domestic animals. For example, the Asian tiger mosquito, originally from Southeast Asia, has spread to many parts of the world andis a known carrier of diseases such as dengue fever, Zika virus, and chikungunya. These diseases can have severehealth consequences for individuals and communities.中文回答:外来物种入侵,也被称为异种或外来物种,指的是那些不是特定生态系统原生物种的植物、动物或微生物,它们有可能对环境、经济或人类健康造成危害。
日本《外来入侵物种法》(INVASIVE ALIEN SPECIES ACT)
INVASIVE ALIEN SPECIES ACT(Law No. 78 (June 2, 2004))[CONTENTS]Chapter 1: General Provisions (Article 1 to Article 3)Chapter 2: Regulations on Handling Invasive Alien Species(Article 4 to Article 10) Chapter 3: Mitigation of Invasive Alien Species (Article 11 to Article 20) Chapter 4: Uncategorized Alien Species (Article 21 to Article 24)Chapter 5: Miscellaneous Provisions (Article 25 to Article 31)Chapter 6: Penal Provisions (Article 32 to Article 36)Supplementary ProvisionsCHAPTER 1: GENERAL PROVISIONS(Purpose)Article 1: This Law shall have the purpose of preventing Adverse Effects on Ecosystems caused by Invasive Alien Species (IAS) through regulating raising, planting, storing, carrying (hereinafter “Raising”), importing, or other handling of invasive alien species and through taking measures such as the mitigation of IAS by the national government and other entities, with the aim to help stabilize and improve national life through contributions to conservation of biodiversity, human safety and sound development of agriculture, forestry and fisheries.(Definition)Article 2: In this Law, “Invasive Alien Species” or “IAS” shall mean individuals (including eggs, seeds and others stipulated by the Cabinet Ordinance;limited to living ones) and their organs (limited to those which require measures such as regulations on Raising for preventing Adverse Effects on Ecosystems to be taken under this Law and which are stipulated by the Cabinet Ordinance (limited to living ones)) that are stipulated by the CabinetOrdinance to exist outside their original habitats as a result of introduction from overseas into our country (hereinafter “Alien Species”) and that are recognized or feared to cause Adverse Effects on Ecosystems because of their different properties from organisms having original habitats in Japan (hereinafter “Indigenous Species”).2. In this Law “Adverse Effects on Ecosystems” shall mean adverse effects onecosystems, human safety, or agriculture, forestry and fisheries.3. When the competent ministers make a plan in enacting, amending orabolishing the ordinance of Paragraph 1, the ministers must consult academic experts on properties of living organisms about the draft plan.(Basic Policy for Preventing Adverse Effects on Ecosystems Caused by Invasive Alien Species)Article 3: The competent ministers shall prepare a draft of a basic policy for preventing Adverse Effects on Ecosystems caused by IAS upon consultation with the Central Environment Council and ask for a Cabinet decision on it. 2. The basic policy in the preceding paragraph (hereinafter “The BasicPolicy”) shall stipulate the following matters:i) The basic framework about the prevention of Adverse Effects onEcosystems caused by IAS;ii) Principles concerning the selection of IAS;iii) Principles the handling of IAS;iv) Principles concerning the mitigation of IAS by the national government and other entities; andv) In addition to those mentioned in the preceding subparagraphs, important matters concerning the prevention of Adverse Effects on Ecosystems caused by IAS.3. The competent ministers must, when the Cabinet decision on The BasicPolicy stipulated under Paragraph 1 is made, announce it officially without delay.4. The provisions of Paragraph 1 and the preceding paragraph shall beapplied mutatis mutandis to a change of The Basic Policy.CHAPTER 2: REGULATIONS ON HANDLINGINVASIVE ALIEN SPECIES(Prohibition of Raising)Article 4: No approval shall be issued to Raising IAS otherwise than in accordance with the following cases:i) When permission in Paragraph 1 of the next Article is obtained andRaising in connection with that permission is performed; orii) In the case of capture and other treatment for mitigation under the provisions of Chapter 3, or when there is an unavoidable reason stipulated in the Ministerial Ordinance.(Permission for Raising)Article 5: A person who wishes to perform Raising of IAS for the purpose of scientific research or any other purposes stipulated by the Ministerial Ordinance must obtain permission from the competent ministers.2. A person who wishes to obtain permission in the preceding paragraphmust submit an application for permission to the competent ministers as stipulated in the Ministerial Ordinance.3. The competent ministers must not grant permission in Paragraph 1 in casethere is a reason that falls under any of the following subparagraphs with respect to the Raising for which the application in the preceding paragraph is submitted:i) The purpose of the Raising does not conform with one stipulated inParagraph 1; orii) A person who is to perform Raising is recognized not to handle IAS properly because the person does not have a facility for the Raising which meets standards stipulated by the Ministerial Ordinance in accordance with the properties of IAS (hereinafter “Special Raising Facility”) or for some other reasons.4. In the case of granting permission in Paragraph 1, the competent ministersmay attach conditions to the permission when they are recognized to be necessary for preventing Adverse Effects on Ecosystems caused by IAS,within the limits of the necessity.5. A permittee in Paragraph 1 must, when performing the permitted Raising,inspect the Special Raising Facility for the permitted IAS periodically, make it clear that the permission is granted for the IAS, and use other methods stipulated in the Ministerial Ordinance.(Order for Measures to Permittees for Raising)Article 6: When a permittee in Paragraph 1 of the preceding Article violates the provisions of Paragraph 5 of the same Article or does not meet conditions imposed under the provisions of Paragraph 4 of the same Article, the competent ministers may order to correct the methods of Raising the IAS or to take other necessary measures if they are recognized to be necessary for preventing Adverse Effects on Ecosystems caused by the IAS.2. The competent ministers may cancel the permission in Paragraph 1 of thepreceding Article in case the permittee violates the provisions of this Law or ordinances based on this Law, or disobeys proceedings imposed by this Law, resulting in the IAS being recognized as having or being likely to have Adverse Effects on Ecosystems.(Prohibition of Import)Article 7: IAS must not be imported. This does not apply, however, to the case where a permittee under Paragraph 1 of Article 5 imports IAS in connection with that permission.(Prohibition of Transfers)Article 8: Any actions relating transfers (hereinafter “Transfers”) of IAS are not allowed. Nevertheless, this does not apply to the case where persons, who perform or intend to perform Raising of IAS in conformity with the provisions of Article 4, Subparagraph 1, shall conduct Transfers of the IAS between them, or to the cases stipulated by the Ministerial Ordinance.(Prohibition of Releasing, Planting, or Sowing)Article 9: IAS regarding Raising, import, or Transfers must not be released,planted, or sowed outside the Special Raising Facility for the IAS.(Collection of Reports and On-site Inspection)Article 10: Within the limits required for the enforcement of this Law, the competent ministers may request a permittee under Paragraph 1 of Article 5 to submit reports on conditions of handling IAS and on other necessary matters, or may authorize staff members to enter facilities for the Raising of IAS, to inspect IAS, documents, and other properties, or to question relevant persons.2. The staff members in the preceding paragraph must carry theiridentification papers and present them to relevant persons.3. The authority under the provisions of Paragraph 1 shall not be construedas being permitted for the purpose of criminal investigation.CHAPTER 3: MITIGATION OF INVASIVE ALIEN SPECIES (Mitigation by the National Government)Article 11: In case Adverse Effects on Ecosystems by IAS occur or are likely to occur, and if a need arises for preventing occurrence of the adverse effects, the competent ministers and heads of the pertinent administrative organs of the national government (hereinafter “the National Government”) shall conduct mitigation under the provisions of this Chapter.2. To perform mitigation under the provisions of the preceding paragraph,the National Government must, in accordance with the Ministerial Ordinance, stipulate the matters mentioned below and announce them officially in consultation with the prefectures concerned.i) The type of IAS to be subjected to the mitigation;ii) An area and a period for which the mitigation is performed; andiii) Details of the mitigation such as capture, collection, or killing (herein after “Capture”) of the IAS and other pertinent matters; andiv) In addition to those mentioned in the preceding subparagraphs, matters stipulated in the Ministerial Ordinance.(Exception from the Wildlife Protection and Hunting Law)Article 12: To the Capture of IAS subjected to mitigation performed by the National Government under the provisions of Paragraph 1 of the preceding Article, the provisions of the Wildlife Protection and Hunting Law (Law No.88 (2002)) shall not be applied.(Entry into Land and other measures)Article 13: Within the limits required for mitigation under the provisions of Article 11, Paragraph 1, the National Government may authorize its staff members to enter other persons’ lands or water surfaces, to conduct Capture of IAS, or to cut down trees and bamboos which interfere with Capture of the IAS.2. In the case of authorizing the staff members to act under provisions of thepreceding paragraph, the National Government, in advance, must notify occupants of the lands or the water surfaces, or owners of the trees and bamboos about the acts, and give an opportunity to express their opinions. 3. The staff members in Paragraph 1 must carry their identification papersand present them to relevant persons.(Compensation of Loss)Article 14: To a person who suffers a loss as a result of an act under the provisions of Paragraph 1 of the preceding Article, the government shall compensate for a loss that is to incur normally.2. A person who wishes to be given compensation under the provisions of thepreceding paragraph needs to request it from the National Government.3. The National Government must, when a request under the provisions ofthe preceding paragraph is received, decide the amount of compensation and notify it to the claimant.(Filing of a Suit)Article 15: A person who is dissatisfied with a decision made under the provisions of Paragraph 3 of the preceding Article may demand an increase of the amount to be given in compensation within six months from the date ofthe receipt of the notice.2. With regard to the complaint under the preceding paragraph, thegovernment shall be the defendant.(Liability of a Causer)Article 16: In case the need to carry out mitigation under the provisions of Paragraph 1 of Article 11 arises and there is a person who has performed an act causing it, the government may make the person bear the whole or part of expenses within the limits necessary to carry out the mitigation.(Methods of Collecting Expenses Imposed)Article 17: When intending to make a person bear expenses under the provisions of the preceding Article, the National Government must fix the amount of expenses intended to make the person bear (hereinafter “Expenses Imposed”in this Article) and the deadline for their payment, and order the payment, as stipulated by the Ministerial Ordinance.2. If there is a person who does not pay Expenses Imposed by the deadlineunder the preceding paragraph, the National Government must urge the person to pay by designating a new deadline in a reminder, as stipulated in the Ministerial Ordinance.3. When the payment is urged under the provisions of the precedingparagraph, the National Government may collect arrearages in an amount calculated by multiplying the Expenses Imposed by a rate of 14.5% or less per annum for the number of days from the date following the deadline for payment in Paragraph 1 to the date of completion of the payment of the Expenses Imposed or to the date preceding the attachment of property for collecting the Expenses Imposed, as stipulated by the Ministerial Ordinance.4. When a person who is urged to pay under the provisions of Paragraph 2does not pay the Expenses Imposed and the arrearages of the Expenses Imposed stipulated by the preceding paragraph (hereinafter “Arrearages” in this Article) by a deadline designated by a reminder in Paragraph 2, the National Government may collect the Expenses Imposed and the Arrearages in accordance with cases of disposition for failure to pay national taxes. Inthis case, the order of the preferential right on the Expenses Imposed and the Arrearages shall come next to national taxes and local taxes.5. The Arrearages shall come prior to the Expenses Imposed.(Mitigation by Others than the National Government)Article 18: On mitigation of IAS which is intended by a local public entity and conforms with matters announced officially under the provisions of Paragraph 2 of Article 11, the local pubic entity may obtain confirmation to that effect from the competent ministers, as stipulated in the Ministerial Ordinance.2. A person other than the government and local public entities may obtainthe competent ministers’ acknowledgement, as stipulated by the Ministerial Ordinance, on the mitigation of IAS planned by the person to the effect that the person is capable of performing it properly and reliably and that the mitigation conforms with matters announced officially under the provisions of Paragraph 2 of Article 11.3. When the competent ministers give confirmation under Paragraph 1 oracknowledgement under the preceding paragraph, that fact must be announced officially as stipulated in the Ministerial Ordinance. The same applies to cases where these confirmation and acknowledgement are cancelled under the provisions of Paragraph 2 or 3 of Article 20.4. The provisions of Article 12 shall be applied mutatis mutandis tomitigation which is performed by a local public entity under the confirmation in Paragraph 1 and mitigation which is performed by a person other than the government and local public entities under the acknowledgement in Paragraph 2, and the provisions of Article 13 to the preceding Article shall be applied mutatis mutandis to local public entities taking charge of affairs related to the mitigation under the confirmation in Paragraph 1.Article 19: The competent ministers may request a person who obtains the acknowledgement in Paragraph 2 of the preceding Article and performs mitigation to submit reports on how the mitigation is performed and on other necessary matters.Article 20: When a person who obtains the confirmation under Article 18,Paragraph 1 or the acknowledgement in Paragraph 2 of the same Article suspends the mitigation or becomes unable to perform the mitigation in conformity with matters announced officially under the provisions of Article 11, Paragraph 2, the person must notify the effect to the competent ministers.2. When notified under the provisions of the preceding paragraph, thecompetent ministers shall cancel the case’s confirmation under Paragraph 1 of Article 18 or its acknowledgement under Paragraph 2 of the same Article. 3. When it is recognized that mitigation on which acknowledgement underParagraph 2 of Article 18 is given is not performed in conformity with matters announced officially under the provisions of Article 11, Paragraph 2, or that a person, who performs the mitigation, becomes unable to carry out the mitigation properly and reliably, omits submitting reports stipulated in the preceding Article, or submits a false report, the competent ministers may cancel the acknowledgement.CHAPTER 4: UNCATEGORIZED ALIEN SPECIES (Notification of Import)Article 21: As stipulated in the Ministerial Ordinance, a person who intends to import uncategorized alien species (which mean Alien Species stipulated in the Ministerial Ordinance as being suspected to have likelihood of causing Adverse Effects on Ecosystems due to properties different from those of Indigenous Species (limited to living ones). Hereinafter the same definition applies.) must previously notify the competent ministers of the type of the uncategorized alien species (or “UAS”) and other matters stipulated in the Ministerial Ordinance.(Judgment)Article 22: When a notification stipulated under the preceding Article is received, the competent ministers must judge whether or not the UAS in the notification has the likelihood of causing Adverse Effects on Ecosystems due to its properties different from those of Indigenous Species, and inform the result to the person who has submitted the notification within six monthsfrom the date of the receipt of the notice.(Restrictions on Import)Article 23: A person who intends to import UAS must not import the UAS before receiving the information under the preceding Article to the effect that the UAS is free from the likelihood of causing Adverse Effects on Ecosystems due to its properties different from those of Indigenous Species.(Uncategorized Alien Species relevant to Exporters Abroad)Article 24: A person who wishes to export UAS to Japan is able to previously notify, as stipulated in the Ministerial Ordinance, the competent ministers of the type of the UAS and other matters stipulated in the Ministerial Ordinance.2. The provisions of Article 22 shall apply mutatis mutandis to thenotification stipulated in the preceding paragraph.CHAPTER 5: MISCELLANEOUS PROVISIONS (Attachment of a Certificate for Import)Article 25: Other organisms (limited to living ones) than those stipulated in the Ministerial Ordinance as being easily confirmable that they do not fall under the category of IAS nor UAS must not be imported unless certificates issued by foreign government agencies proving the types of the organisms or stipulated in the Ministerial Ordinance are attached to the organisms.2. An organism requiring the attachment of a certificate in the precedingparagraph must not be imported through any other place than a port or an airport stipulated in the Ministerial Ordinance.(Personnel Engaging in Control)Article 26: The competent ministers may authorize those of staff members who meet requirements stipulated by the Cabinet Ordinance to exercise a part of authorities stipulated in Paragraph 1 of Article 6 or Paragraph 1 or Article 10.2. Staff members who exercise the part of authorities of the competentministers under the provisions of the preceding paragraph (in the next paragraph, “Controllers for IAS’ Adverse Effects Prevention”) must carry their identification papers and present them to relevant persons when such authorities are to be exercised.3. In addition to those stipulated in the preceding two paragraphs, mattersnecessary in relation to the Controllers for IAS’ Adverse Effects Prevention shall be stipulated by the Cabinet Ordinance.(Measures for Amplification of Scientific Knowledge)Article 27: For the sake of amplification of scientific knowledge about Adverse Effects on Ecosystems caused by Alien Species and the prevention thereof, the government must endeavor to collect, arrange and analyze information, promote study, and take other necessary measures relevant to the knowledge.(Promotion of Public Understanding)Article 28: About mitigating IAS and other matters involved with Alien Species, the government must endeavor to deepen public understanding through measures such as educational activities and public relation activities.(The Competent Ministers and the Ministerial Ordinance)Article 29: The competent minister in this Act shall be the Minister of the Environment. Nevertheless, for matters related to the prevention of adverse effects on agriculture, forestry and fisheries, the Minister of the Environment and the Minister of Agriculture, Forestry and Fisheries shall be the competent ministers.2. The Ministerial Ordinance in this Act shall be an order issued by thecompetent ministers.(Interim Measures)Article 30: In case an order is established, amended or abolished under the provisions of this Act, needed interim measures (including interim measures on penal provisions) may be stipulated by the order to the degree judged reasonably necessary for the establishment, amendment or abolition thereof.(Delegation to the Ministerial Ordinance)Article 31: Besides those stipulated in this Act, procedures for the implementation of this Act and other matters necessary for the enforcement of this Act shall be stipulated by the Ministerial Ordinance.CHAPTER 6: PENAL PROVISIONSArticle 32: A person who falls under any of the following subparagraphs shall be punished by imprisonment for any period not exceeding three years or a fine not exceeding three million yen, or a combination of these two.i) A person who has performed Raising of IAS with the aim to sell ordistribute in violation of the provisions of Article 4;ii) A person who has obtained permission in Paragraph 1 of Article 5 by a deception or other unlawful means;iii) A person who has disobeyed an order under the provisions of Article 6, Paragraph 1;iv) A person who has violated the provisions of Article 7 or Article 9; orv) A person who has sold or distributed IAS in violation of the provisions of Article 8.Article 33: A person who falls under any of the following subparagraphs shall be punished by imprisonment for any period not exceeding one year or a fine not exceeding one million yen, or a combination of these two.i) A person who has violated the provisions of Article 4 or Article 8(excluding those who fall under Subparagraph 1 or Subparagraph 5 of the preceding Article);ii) A person who has performed Raising of IAS against conditions attached under the provisions of Article 5, Paragraph 4; oriii) A person who has violated the provisions of Article 23.Article 34: A person who has violated the provisions of Paragraph 1 or Paragraph 2 of Article 25 shall be punished by a fine not exceeding five hundred thousand yen.Article 35: A person shall be punished by a fine not exceeding three hundredthousand yen who has not submitted reports or has submitted a false report under the provisions of Paragraph 1 of Article 10; or who has refused, disturbed or evaded an on-site inspection under the provisions of the same paragraph, or has not given a statement or has given a false statement in reply to a question asked at the on-site inspection.Article 36: In case a representative of a corporation, or an agent, an employee or other operative of a corporation or a person commits an offense in Article 32 to the preceding Article in connection with the work of the corporation or the person, besides punishing the actual offender, the corporation is punished bya fine stipulated in an appropriate one of the following subparagraphs andthe person is punished by a fine set forth in the main text of each appropriate Article.i) Article 32: Punishment by a fine not exceeding one hundred million yenii) Article 33: Punishment by a fine not exceeding fifty million yeniii) Article 34 or Article 35: Punishment by a fine set forth in the main text of each appropriate ArticleSUPPLEMENTARY PROVISIONS(Date of Enforcement)Article 1: This Act shall be enforced from a date stipulated by the Cabinet Ordinance within the limits not exceeding one year from the date of promulgation. Nevertheless, the provisions of the next Article, Article 3 and Article 5 of Supplementary Provisions shall be enforced from the date of promulgation.(Interim Measures)Article 2: Even before the enforcement of this Act, the competent ministers may prepare a basic policy for preventing Adverse Effects on Ecosystems caused by IAS in accordance with cases in the provisions of Paragraph 1 and Paragraph 2 of Article 3 and ask for a Cabinet decision.2. When the Cabinet decides on the basic policy in the preceding paragraph,the competent ministers must announce it officially without delay.3. The basic policy set forth under the provisions of Paragraph 1 shall betaken as The Basic Policy stipulated under the provisions of Paragraph 1 and Paragraph 2 of Article 3 on the date of enforcement of this Act.(Delegation to the Cabinet Ordinance)Article 3: Besides those stipulated in the preceding Article, necessary interim measures concerning the enforcement of this Act shall be stipulated by the Cabinet Ordinance.(Review)Article 4: The government shall, after five years lapse from the enforcement of this Act, conduct a review concerning the state of enforcement of this Act and, when it is deemed necessary, shall devise requisite measures based on the results thereof.(Partial Amendment of the Basic Environment Law)Article 5: Part of the Basic Environment Law (Law No. 91 (1993)) shall be amended as follows:Article 41, Paragraph 2, Subparagraph 3 shall be amended as follows:iii) To deal with matters caused to pertain to their authorities by the Natural Park Law (Law No. 161 (1957)), the Farmland Soil Pollution Control Law (Law No. 139 (1970)), the Natural Environment Conservation Law (Law No. 85 (1972)), the Protection and Keeping of Animals Law (Law No. 105 (1973)), the Special Measures Law for Conservation of Seto-Inland Sea Environment (Law No. 110 (1973)), the Law concerning Compensation for Pollution Damage to Health (Law No. 111 (1973)), the Law for the Conservation of Endangered Species of Wild Fauna and Flora (Law No. 75 (1992)), the Special Measures Law on Dioxins (Law No. 105 (1999)), the Basic Law for Recycling-oriented Society Promotion (Law No. 110 (2000)), the Law concerning Recycling of Used Motor Cars (Law No. 87 (2002)), the Wildlife Protection and Hunting Law (Law No. 88 ( 2002)) and the Invasive Alien Species Act (Law No. (2004)).REASONS FOR INTRODUCING THIS BILLIn order to prevent adverse effects on ecosystems, human safety, or agriculture, forestry and fisheries caused by Invasive Alien Species, raising, planting, storing or carrying, importing and other handling of IAS are prohibited with the exception of specified cases. At the same time, the mitigation of IAS by the government and other entities is promoted. Besides, it is necessary to restrict the import of Uncategorized Alien Species and to take other requisite measures. These are reasons for introducing this bill.。
最新TPO31阅读文本答案及译文
Geographic isolation also can proceed slowly, over great spans of time. We find evidence of such extended events in the fossil record, which affords glimpses into the breakup of formerly continuous environments. For example, during past ice ages, glaciers advanced down through North America and Europe and gradually cut off parts of populations from one another. When the glacier retreated, the separated populations of plants and animals came into contact again. Some groups that had descended from the same parent population were no longer reproductively compatible — they had evolved into separate species. In other groups, however, genetic divergences had not proceeded so far, and the descendants could still interbreed — for them, reproductive isolation was not completed, and so speciation had not occurred.
雅思作文政府寻找生命在其他星球
雅思作文政府寻找生命在其他星球In recent years, the idea of searching for life on other planets has gained significant attention. With the advancement of technology and the exploration of outer space, the possibility of finding life beyond Earth has become a topic of interest for many. In this essay, I will discuss the government's role insearching for life on other planets, the potential benefits and challenges of such a mission, and the ethical considerations that come with this endeavor.First and foremost, the government plays a crucial role in funding and organizing space exploration missions. The search for life on other planets requires significant resources, expertise, and coordination, which are often beyond the capabilities of private organizations. Therefore, it is theresponsibility of the government to allocate funds and support research in this field. By investing in the search for extraterrestrial life, the government can contribute to scientific advancements and potentially make groundbreaking discoveries that could benefit humanity as a whole.Moreover, the government's involvement in the search for life on other planets can also have geopolitical implications. In the current space race, various countries are competing to establish their dominance in outer space. By leadingthe effort to find life beyond Earth, a government can enhance its reputation as a leader in space exploration and demonstrate its technological prowess to the world. This can have diplomatic and strategic advantages, as it may strengthen acountry's position in international relations and collaborations.However, the search for life on other planets also poses significant challenges. The vastness of space and the limitations of current technology makeit extremely difficult to detect signs of life in distant planets. Furthermore,the cost of space exploration is exorbitant, and there is no guarantee of success. Governments must weigh the potential benefits of such missions against the high costs and risks involved. Additionally, the ethical implications of searching for extraterrestrial life cannot be overlooked.One of the ethical considerations is the potential impact on existing life forms in space. If life is discovered on another planet, it raises questions about how we should interact with and study these life forms. There is a risk of contaminating alien ecosystems with Earth-based organisms, which could have detrimental effects on the newly discovered life. Governments must establishstrict guidelines and protocols to ensure that any interaction withextraterrestrial life is conducted in a responsible and ethical manner.Furthermore, the discovery of extraterrestrial life could have profound implications for humanity's worldview and belief systems. It may challenge religious and philosophical perspectives on the uniqueness of life on Earth and our place in the universe. Governments must consider the potential societal and cultural impacts of such a discovery and prepare for the ethical and moral debates that may arise.In conclusion, the government plays a pivotal role in the search for life on other planets. While there are potential benefits to be gained from such missions, including scientific advancements and geopolitical advantages, there are also significant challenges and ethical considerations that must be addressed. As we continue to explore the cosmos, it is essential for governments to approach the search for extraterrestrial life with careful consideration and a commitment to ethical conduct.。
2023届高考英语二轮复习外刊阅读理解训练大西洋森林
23年高考英语外刊阅读理解训练——大西洋森林——改编自The Atlantic Forest The Atlantic Forest in Brazil is one of the world's most threatened rainforests and also a UNESCO World Heritage site. Over 80 percent of its tree cover has been lost due to climate change and human activities. Nevertheless, new research suggests that restoring the forest could protect endangered species and water resources while making it more resilient to climate change.Ecotourism is emerging as a way to conserve the remaining seven percent of the forest and boost Brazil's economy. Among the forest's natural wonders are bioluminescent mushrooms and hundreds of caves. The Ribeira Valley offers the forest's largest intact area with biodiversity rivaling the Amazon.Visitors can participate in nighttime hunts for glowing mushrooms at the IPBio Betary Reserve, which covers 148 acres of rainforest dedicated to conservation, research, andsustainable tourism. These tours teach travelers about IPBio's research while funding further scientific study and conservation at the reserve. Of approximately 100 bioluminescent mushroom species identified worldwide, 27 have been found in the reserve.University of São Paulo associate professor Cassius Stevani leads these treks monthly, except in August and September, for anyone interested in learning about the unique ecology. The Atlantic Forest is home to Indigenous communities and over 145 million Brazilians, and by experiencing its remnants, visitors can contribute to the rural economy while improving locals' quality of life.【重点词汇】1. Atlantic [əˈtlæntɪk] adj. 大西洋的2. forest ['fɔrɪst] n. 森林3. Brazil [brəˈzɪl] n. 巴西4. threaten ['θrɛtn] v. 威胁5. rainforest ['renfɔrɪst] n. 热带雨林6. UNESCO ['ju:nɛskoʊ] n. 联合国教科文组织7. World Heritage 世界遗产8. site [saɪt] n. 地点9. percent [pər'sent] n. 百分之10. tree cover 树木覆盖11. climate change 气候变化12. human activities 人类活动13. restore [rɪˈstɔr] v. 恢复14. protect [prəˈtɛkt] v. 保护15. endangered species 濒危物种16. water resources 水资源17. resilient [rɪˈzɪljənt] adj. 有弹性的,能恢复的18. ecotourism ['i:kotʊrɪz(ə)m] n. 生态旅游19. conserve [kənˈsɜrv] v. 保存20. boost [bu:st] v. 促进,提高21. economy [i'kɔnəmi] n. 经济22. natural wonders 自然奇观23. bioluminescent [ˌbaɪoʊlu:mɪ'nesnt] adj. 生物发光的24. mushroom ['mʌʃrʊm] n. 蘑菇25. cave [keɪv] n. 洞穴26. Ribeira Valley 里贝拉山谷27. intact [ɪn'tækt] adj. 完整的28. biodiversity 生物多样性29. rival [ˈraɪvl] v. 相匹敌30. Amazon ['æməzɔn] n. 亚马逊31. participate [pɑr'tisipeit] v. 参与32. nighttime [ˈnaɪttaɪm] n. 夜间33. hunt [hʌnt] v. 狩猎34. IPBio Betary Reserve IPBio Betary 保护区35. stretch [strɛtʃ] n. 区域,范围36. research [rɪ'sɜrtʃ] n. 研究37. sustainable [(s)ə'steinəbl] adj. 可持续的38. teach [ti:tʃ] v. 教授39. scientific study 科学研究40. professor [prə'fɛsə(r)] n. 教授41. unique ecology 独特的生态系统42. home [həʊm] n. 家园43. Indigenous [ɪn'dɪʤɪnəs] adj. 土著的,原住民的44. contribute [kənˈtrɪbju:t] v. 贡献45. rural ['rʊrəl] adj. 农村的46. economy [i'kɔnəmi] n. 经济47. improve [ɪm'pru:v] v. 改善48. locals [ˈləʊkəlz] n. 当地人49. quality of life 生活质量50. experience [ɪksˈpɪriəns] v. 经历【阅读理解练习题】1. What makes the Atlantic Forest in Brazil unique?A. It is home to bioluminescent mushrooms.B. It has the largest area of biodiversity in the world.C. It is a UNESCO World Heritage site.D. It is one of the largest rainforests in the world.答案:C。
英语作文外来物种入侵孙教授讲座
英语作文外来物种入侵孙教授讲座Ladies and gentlemen,。
Good afternoon! Today, I am honored to have the opportunity to give a lecture on the topic of invasive alien species. As we all know, invasive alien species refer to non-native organisms that are introduced into a new environment and have the potential to cause harm to the native ecosystem. It is a global issue that requires our immediate attention and action.Firstly, let us delve into the reasons behind the introduction of invasive alien species. Human activities, such as international trade, travel, and tourism, play a significant role in the spread of these species. With the increasing globalization, the transportation of goods and people has become more frequent, inadvertently facilitating the movement of non-native species across borders. Moreover, climate change and habitat destruction have also contributed to the establishment and spread of invasive alien species.Now, let us explore the impacts of invasive alien species on ecosystems. These species often outcompete native species for resources, leading to a decline in biodiversity. They can disrupt the natural balance of ecosystems, causing irreversible damage. For example, the red lionfish, native to the Indo-Pacific region, has become an invasive species in the Caribbean Sea and the Atlantic Ocean. Its voracious appetite and lack of natural predators have resulted in the decimation of native fish populations and the degradation of coral reefs.In addition to ecological impacts, invasive alien species can also have severe economic and social consequences. They can damage crops, forests, and infrastructure, leading to substantial financial losses. For instance, the emerald ash borer, a beetle native to Asia, has caused extensive damage to ash trees in North America, resulting in billions of dollars in economic losses. Furthermore, invasive species can affect human health by transmitting diseases or causing allergic reactions.To address this issue, it is crucial to implement effective management strategies. Prevention is the most cost-effective approach, focusing on measures such as stricter border controls, quarantine regulations, and public awareness campaigns. Early detection and rapid response are also essential in eradicating or controlling invasive species. This includes monitoring and surveillance programs, as well as the development of innovative techniques for their management.International cooperation is paramount in combating the invasion of alien species. Collaboration between countries, sharing of information and expertise, and the establishment of global frameworks and agreements are crucial steps in addressing this global challenge. Furthermore, public involvement and engagement are vital in raising awareness and promoting responsible behavior towards the prevention and management of invasive species.In conclusion, the invasion of alien species poses a significant threat to our ecosystems, economies, and societies. It is imperative that we take immediate action to prevent and control their spread. Through international cooperation, effective management strategies, and public engagement, we can mitigate the impacts of invasive alien species and protect our precious natural resources for future generations.Thank you for your attention, and I hope this lecture has provided you with valuable insights into the issue of invasive alien species. Let us work together to preserve the biodiversity and integrity of our ecosystems.。
2022考研英语阅读侵略性物种
2022考研英语阅读侵略性物种Invasive species侵略性物种Thorny questions麻烦问题The ecological effects of buckthorn in NorthAmerica北美鼠李属植物的生态影响CONSERVATIONISTS, being by definition conservative, usually view the introduction ofnew species into an environment with horror.生态环境爱护者,从定义上看就偏于保守,常对固有环境中新物种的引入恐惊不已。
If such a species is successful, it is described as invasivea rather pejorative word.一种新物种一旦引入胜利,它时常具有侵略性一个含贬义的词语。
But how much change such species actually cause is often moot.然而,这些物种毕竟造成环境多少转变?So two recent studies of European buckthorn in North America, which attempt to find thisout, are a welcome shaft of light on the debate.时常引来争辩。
最近对鼠李属植物的两项讨论有助于搞清这一问题。
所以该讨论在这场争辩中受人瞩目。
Buckthorn was imported from Europe to America in the 19th century, to make gardenhedges.鼠李属植物在19世纪从欧洲出口到美国,用来制作花园围篱。
Since then it has spread through thecountry s woodlands, which many naturalists think has been bad for local wildlife.从那时起,它席卷了美国林地。
高考英语外刊时文精读专题07入侵物种地下杀手
2023年高考英语外刊时文精读精练 (7)Invasive species入侵物种News from the underground地下“杀手”主题语境:人与自然主题语境内容:人与环境、人与动植物【外刊原文】(斜体单词为超纲词汇,认识即可;下划线单词为课标词汇,需熟记。
)E arthworms’kindly image as aerators(通气设备), drainers(滤干器) and fertilisers(肥料) of field and garden buries a darker secret.They are actually fierce competitors withother invertebrates(无脊椎动物), consuming rotting(腐烂的) plant matter and tiny organisms , all of which might otherwise threaten a wide variety of soil dwellers(居民).That much is well known, not least from research conducted in northern North America. Here, worms were wiped out during the last ice age, which ended 12,000 years ago. They started returning, in the form of European invaders(入侵者), only a few centuries in the past. What have not been investigated much until now are the consequences of this underground killing for surface-living creatures. But that has just been corrected by Malte Jochum of Leipzig University, in Germany, and his colleagues, in a study just published in Biology Letters.Dr Jochum and his team worked in a forest overlooking Barrier Lake, in Alberta, Canada, where the earthworm invasion has been tracked for three decades. That has permitted the identification of areas with low (four worms per square metre, on average), medium(43 worms per square metre) and high (106 per square metre) populations.Within each zone of abundance,the researchers marked 20 plots with individual areas of two square metres. They identified all of the plants and used vacuum-suction collecting devices(真空吸力收集装置) to collect as many as possible of the above-surface arthropods(地表节肢动物) in each plot,,mostly insects and spiders . They then sorted, identified and measured these animals to calculate their abundance, biomass(生物量)and species richness.(Species abundance refers to the number of individuals per species. species richness refers to the number of species in an area.)Altogether, the collectors picked up 13,037 individual arthropods(节肢动物)—and differences between plots were quickly obvious. Those with abundant earthworms were shorter of arthropods compared with ones where worms were rare.Plots with the most worms in them had 61% fewer individual arthropods, 18% fewer arthropod species and a 27% reduction in total arthropod biomass, compared with those with the fewest.So-called detritivores(屑食生物)—which compete directly with worms for food—suffered worst. There were 80% less of them in areas of worm abundance, compared with those of less worm . But herbivores and omnivores(食草动物和杂食动物)suffered, too. Only for carnivorous arthropods(食肉节肢动物), such as spiders, was there good news. Their numbers were up 41% in worm-rich plots, compared with worm-poor ones.Why predators did well is unclear. Some, perhaps, were eating worms directly. Others may have takenadvantage of the removing of cover for their prey(猎物) caused by worms pulling the leafunderground for later consumption.The knock-on effects of this “killing”further up the food chainremain unclear. Species that liketo eat worms are possibly doing better, while those that prefer their meals crunchy(松脆) will be doing worse. Whether this matters in the grand scheme of things is debatable. But for those who prefertheir ecosystems primitive, this work confirms that earthworms are certainly not the purely good which some people make them out to be.【课标词汇】1.fierce猛烈的;激烈的;骇人的•a fierce attack/battle猛烈的进攻/激烈的战斗Two men were shot during fierce fighting last weekend.上周末的激战中两人被枪击。
专业英语四级模拟试卷及答案解析(14)
专业英语四级模拟试卷及答案解析(14)(1/1)PART I DICTATIONPlay00:0012:06Volume第1题Listen to the following passage. Altogether the passage will be read to you four times. During the first reading, which will be read at normal speed, listen and try to understand the meaning. For the second and third readings, the passage will be read sentence by sentence, or phrase by phrase, with intervals of 15 seconds. The last reading will be read at normal speed again and during this time you should check your work. You will then be given 2 minutes to check through your work once more.Please write the whole passage on ANSWER SHEET ONE.下一题(2~4/共10题)PART ⅡLISTENING COMPREHENSIONSECTION A TALKIn this section you will hear a talk.You will hear the talk ONCE ONLY.While listening, you may look at ANSWER SHEET ONE and write NO MORE THAN THREE WORDS for each gap.Make sure what you fill in is both grammatically and semantically acceptable.You may use the blank sheet for note-taking.You have THIRTY seconds to preview the gap-filling task.Now listen to the talk.When it is over, you will be given TWO minutes to check your work. Play00:0000:47Volume第2题What is wrong with Dad?A.He was bad-tempered.B.He must see a doctor.C.He may have a heart disease.D.He may have a headache.第3题What is the relationship between the two speakers?A.Mother and daughter.B.Doctor and patient.C.Teacher and student.D.Friends.第4题Which of the following details is correct?A.Dad used to be bad tempered.B.Dad had a check last month.C.Dad had known his disease.D.The doctor was not sure of Dad"s disease.上一题下一题(5~7/共10题)PART ⅡLISTENING COMPREHENSIONSECTION A TALKIn this section you will hear a talk.You will hear the talk ONCE ONLY.While listening, you may lookat ANSWER SHEET ONE and write NO MORE THAN THREE WORDS for each gap.Make sure what you fill in is both grammatically and semantically acceptable.You may use the blank sheet for note-taking.You have THIRTY seconds to preview the gap-filling task.Now listen to the talk.When it is over, you will be given TWO minutes to check your work. Play00:0001:21Volume第5题What were the two environment campaigners claims against McDonald"s?A.The food carries health risks.B.McDonald"s workers suffer poor pay and conditions.C.Eating the company"s hamburgers can cause heart disease.D.All of the above.第6题How long did the trial last?A.Two years.B.Three years.C.Four years.D.Five years.第7题Which court awarded McDonald" s damages of 60,000 against the two campaigners?A.The High Court in London.B.The High Court in New York.C.The Appeal Court in London.D.The Appeal Court in New York.上一题下一题(8~11/共10题)PART ⅡLISTENING COMPREHENSIONSECTION A TALKIn this section you will hear a talk.You will hear the talk ONCE ONLY.While listening, you may look at ANSWER SHEET ONE and write NO MORE THAN THREE WORDS for each gap.Make sure what you fill in is both grammatically and semantically acceptable.You may use the blank sheet for note-taking.You have THIRTY seconds to preview the gap-filling task.Now listen to the talk.When it is over, you will be given TWO minutes to check your work. Play00:0001:28Volume第8题What is the main topic of the conversation?A.How to have fun in summer.B.How to make money during summer break.C.How to keep the family business during summer break.D.Tentative plans for summer break.第9题What is the woman"s main dilemma?A.Going to Italy or helping her mother.B.Going to Nepal or joining the Air Force.C.Having fun or making money.D.Doing the family duty or improving her engineering skills.第10题How much percent will be raised for engineering fees?A.5%.B.10%.C.15%.D.20%.第11题Which of the following is CORRECT?A.The girl"s friend owns a restaurant in Italy.B.The girl"s father is sick seriously and still stays in hospital.C.The boy could go to Nepal as a volunteer to instruct local residents.D.Students cannot borrow money from financial aid for tuition.上一题下一题(12~14/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEET TWO.You have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:0001:30Volume第12题What is the main topic of the passage?A.The mechanics of rain.B.The climate of North America.C.How gravity affects air current.D.Types of clouds.第13题Why don"t all ice crystals in clouds immediately fall to Earth?A.They are balanced by the pressure of rain droplets.B.The effect of gravity at high altitude is random.C.They are kept in the sky by air current.D.They are moving about with fixed direction.第14题In this passage, what does the term "coalescence" refer to?A.The gathering. of small clouds to form large, clouds.B.The growth of droplets from small to big.C.The fall of raindrops and other precipitationD.The movement of dust particles in the sunlight.上一题下一题(15~17/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEET TWO.You have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第15题We can learn from the passage that ______A.the solar water heaters are very difficult to buildB.the system has been widely usedC.the system is based on a design developed in ArabiaD.the solar water heater consists of three parts第16题Which is the TRUE statement about the collector?A.The collector is made of several kinds of sheets.B.The collector is placed on the water.C.The collector is made of corrugated sheets.D.Not mentioned in the passage.第17题What is the second part of the solar water heater used for?A.Heating the water.B.Letting the water flow out.C.Letting water flow into the system.D.Holding water for the system.上一题下一题(18~20/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEET TWO.You have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第18题The main idea of this passage is ______.A.telling the importance of networkingB.one of your success tools—networkingC.an introduction to the text "the Networking Survival Guide"D.Diane Darling"s opinions on disadvantages of networking第19题Diane Darling is ______.A.the author of the passage you have just beardB.the founder of networkC.the guide of networkingD.the CEO of a Boston-based company第20题The text entitled "The Networking Survival Guide" ______.A.is to help you gain confidenceB.will guide you to find life style that is right for youC.will teach you how to start a new business ventureD.will make you know how to set your networking goals上一题下一题(21~23/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEET TWO.You have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第21题Robert Spring spent 15 yearn ______.A.running a bookstore in PhiladelphiaB.corresponding with Miss Fanny JacksonC.as a forgerD.as a respectable dealer第22题After the Civil War, there was a great demand in Britain for ______.A.southern moneyB.signatures of George Washington and Ben FranklinC.southern manuscripts and lettersD.Civil War plans第23题Who was Miss Fanny Jackson?A.The only daughter of General "Stonewall" Jackson.B.A little-known girl who sold her father"s papers to Robert Spring.C.Robert Spring"s daughter.D.An imaginary person created by Spring.上一题下一题(24~25/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEETYou have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第24题How many students were in this test about economics?A.79,000.B.11,500.C.47,000.D.54,000.第25题Which of the following statements is CORRECT?A.Only a small part of the twelfth-graders have a basic level of understanding of economics.B.The students did better in the economics test than in history or science.C.The tests were given to the university students.D.47 percent of the high school graduates had taken an economics class.上一题下一题(26~27/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEET TWO.You have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第26题Of the 349 forest and grassland fires,A.290 have been extinguished.B.89 have been controlled.C.40 remained out of control.D.7 are in the bordering provinces.第27题The losses caused by the fires includeA.63 men dead.B.26 men injured.C.7,000 heads of livestock dead.D.7 million hectares of forest destroyed.上一题下一题(28~29/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEETYou have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第28题When did the fight begin?A.On Monday.B.On Thursday.C.On Friday.D.On Saturday.第29题What did the protestors use to fight against the riot police?A.Batons.B.Stones.C.Sticks.D.Windows.上一题下一题(30~31/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read the four choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEET TWO.You have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第30题Which of the following statements about stock market indexes is CORRECT, according to the news item?A.Stock market indexes in Shanghai and Sydney rose slightly Friday.B.Stock market indexes dropped sharply around the world Friday.C.S. stock market index didn"t drop because of Obama"s reforms.D.Stock market index in Taiwan dropped most Friday.第31题How much did Japan"s Nikkei index lose Friday?A.More than 2.5 percent.B.Less than 1 percent.C.Between 1 and 2 percent.D.About 1.5 percent.上一题下一题(32~33/共22题)SECTION B CONVERSATIONSIn this section you will hear two conversations.At the end of each conversation, five questions will be asked about what was said.Both the conversation and the questions will be spoken ONCE ONLY.After each question there will be a ten-second pause.During the pause, you should read thefour choices of A, B, C and D, and mark the best answer to each question on ANSWER SHEET TWO.You have THIRTY seconds to preview the questions.Now listen to the conversations.Play00:00…Volume第32题The Austria Big Dry ______.A.has lasted for monthsB.was going to lessen its strength and powerC.was so severe that some land has become dustD.has caused some death第33题What actions have been take by the government?A.Another billion dollars on drought relief will be granted.B.Next week the cabinet would discuss how to fight the drought.C.The Prime Minister was not satisfied with farmers" complaints.D.They pay more attention to farmers" depression and rising debt.上一题下一题(34~53/共20题)PART ⅣCLOZEDecide which of the words given in the box below would best complete the passage if inserted in the corresponding blanks.The words can be used ONCE ONLY.Mark the letter for each word on ANSWER SHEET TWO.The majority of people, about nine out of ten, are right-handed. 1 until recently, people who were left handed were considered 2 , and once children showed this 3 , they were forced to use their right hands. Today left-handedness is generally 4 but it is still a disadvantage in a world 5 most people are right-handed. For example, most tools and implements are still 6 for right-handed people.In sports, 7 contrast, doing things with the left hand or 8 , is often an advantage. Throwing, kicking, punching or batting from the " 9 "side may result in throwing 10 many opponents who are more accustomed to dealing with the 11 of players who are right-handed. This is 12 , in many 13 at a professional level, a bigger 14 of players are left-handed than in the population as a whole.The word "right" in many languages means "correct" or is 15 with lawfulness, whereas the words associated with "left," such as "sinister", generally have 16 associations.In the past, in most Western societies, children were often 17 to use their right hands, especially to write 18 . In some cases the left hand was 19 behind the child"s back so that it could not be used. If, in the future, they are allowed to choose, there will certainly be more left-handers, and probably 20 people with minor psychological disturbances as a result of being forced to use their right hand.第34题A.DownB.NeverC.UpD.NotA.uniqueB.eccentricC.oddD.abnormal第36题A.habitB.tenancyC.tendencyD.trend第37题A.acceptedB.admittedC.approvedD.acknowledged 第38题A.whenB.thatC.whereD.which第39题A.orderedB.designedC.plannedD.supposed第40题A.byB.forC.atD.with第41题A.legB.armC.eyeD.foot第42题A.properB.indirectC.correctD.wrong第43题A.awayB.downC.off第44题A.minorityB.majorityC.plentyck第45题A.the reasonB.the caseC.whyD.that第46题A.gamesB.hobbiesC.activitiesD.rounds第47题A.partB.percentC.proportionD.section第48题A.relatedB.mixedC.connectedbined 第49题A.negativeB.positiveC.constructiveD.doubtful第50题A.allowedB.forcedC.enforcedD.lured第51题A.byB.inC.withD.on第52题A.tiedB.attachedC.broughtD.removed第53题A.noB.moreC.greaterD.fewer上一题下一题(1/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第54题No case is on record of a ______ being ceasing to be ______ under cultivation.A.variable,variantB.variant,variableC.varied,variousD.variable,variable上一题下一题(2/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第55题The new student dare not speak in class. Nor ______ to raise any questions.A.he dareB.dare heC.does he dareD.dares he上一题下一题(3/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第56题I could help him with that, but I would sooner he ______ it by himself.A.doesB.didC.doD.should do上一题下一题(4/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第57题The reason why he has been such a success is ______ he never gives up.A.whatB.thatC.becauseD.how上一题下一题(5/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第58题In many areas, rapid development is the result of ______ in the research laboratory.A.work to doB.work doneC.doing workD.work doing上一题下一题(6/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第59题Another big issue ______ the new republic is the problem of the education of its citizens.A.confiningB.confirmingC.conformingD.confronting上一题下一题(7/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第60题It"s an awful ______ your wife couldn"t come. I was looking forward to meetingA.harmB.sorrowC.shameD.shock上一题下一题(8/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第61题Every member of the original cast was signed ______ her.A.in addition toB.exceptC.except forD.besides上一题下一题(9/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第62题I was to have a trip abroad if ______.A.I had not been firedB.I was not firedC.my boss won"t have fired meD.I were not fired上一题下一题(10/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第63题The hunters desired a clever trap for the animal and it ______ straight into it.A.wentB.fellC.gotD.dropped上一题下一题(11/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第64题Returning to my home, ______.A.my book was missingB.I found my book missedC.I found my book missingD.the book was missed上一题下一题(12/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第65题_________, he is ready to accept suggestions from different sources.A.Instead of his contributionsB.For all his notable contributionsC.His making notable contributionsD.However his notable contributions上一题下一题(13/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第66题You ______ that letter to James. However, you didn"t.A.ought to writeB.ought to have writtenC.should writeD.should be writing上一题下一题(14/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第67题Rather like a spoilt child, he can force you into feeling that his survival depends on your ______ presence and care.A.considerateB.constantC.conscientiousD.consistent上一题下一题(15/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第68题The travelers ______ their journey after a short break.A.recoveredB.resumedC.renewedD.restored上一题下一题(16/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第69题After 10 hours at the wheel of the car, he began to feel the ______.A.tensionB.nervousC.exertionD.strain上一题下一题(17/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第70题We know she was always as ______ as her word, so we trusted her.A.goodB.honestC.faithfulD.true上一题下一题(18/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第71题His maturity appears in the ______ clear-sightedness with which he could observe his own character.A.indifferentB.unconcernedC.detachedD.incurious上一题下一题(19/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第72题The storm sweeping over SW China is sure to lead to ______ of vegetables in the following days.A.validityB.varietyC.scarcityD.rarity上一题下一题(20/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第73题______ of the department, I would like to thank Mr. Jones for his stimulating lecture.A.On behalfB.On accountC.In personD.Instead上一题下一题(21/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第74题Although he thought he was helping us to prepare the dinner, he was actually ______ the way.A.inB.offC.byD.on上一题下一题(22/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第75题There was a ___________ of his latest novel in a local newspaper immediately after its publication.mentB.reviewC.remarkD.revision上一题下一题(23/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第76题Nancy was surprised that they have______.They seemed to be a happy couple.A.split upB.broken downC.fallen throughD.knocked out上一题下一题(24/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第77题Listening to thrilling stories made my flesh______.A.climbB.itchyC.creepD.move上一题下一题(25/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第78题In our highly technological society, the number of jobs for unskilled workers is ______.A.shrinkingB.obscuringC.alteringD.constraining上一题下一题(26/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第79题If we had been more careful, we ______ much better results now.A. would be gettingB. would have gotC. gotD. had gotA.B.C.D.上一题下一题(27/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第80题I don"t ______his idea about how to catch the criminal; I think it"s dangerous.A.go forB.make forC.take forD.call for上一题下一题(28/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第81题Which of the following sentences is INCORRECT?A.I looked at the flowers, not knowing what to say.B.I looked at the flowers, and I didn"t know what to say.C.Looking at the flowers, I didn"t know what to say.D.Looked at the flowers, I didn"t know what to say.上一题下一题(29/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第82题A turn in the road is not the end of the road______you fail to make the turn.A.withoutB.unlessC.becauseD.so that上一题下一题(30/30)PART ⅢLANGUAGE KNOWLEDGEThere are twenty sentences in this section.Beneath each sentence there are four words or phrases marked A, B, C and D.Choose one word or phrase that best completes the sentence.第83题After making a great effort, we finally ______ the plan.A.carried on。
Invasive Aliens Fighting Unwanted Guests
Invasive Aliens Fighting Unwanted Guests Invasive alien species are a significant threat to ecosystems around the world. These species, often introduced by human activities, can outcompete native species for resources, disrupt ecological processes, and even cause economic harm. In many cases, efforts are made to control or eradicate these invasive aliens in order to protect native biodiversity. However, in some cases, these efforts caninadvertently harm other non-native species that are also considered invasive.This raises the question: how do we balance the need to control invasive aliens with the potential harm to other non-native species? One example of this dilemmais the case of invasive plants in a particular region. Let's say that a certain area is being overrun by an invasive plant species that is outcompeting native plants and disrupting the local ecosystem. In an effort to control this invasive plant, herbicides are used, which are effective in reducing the population of the invasive species. However, it is discovered that the herbicides are also harming a non-native plant species that, while also considered invasive, is not having as detrimental an impact on the ecosystem as the first species. This presents a difficult decision for conservationists and land managers: do they continue to use herbicides to control the invasive plant, even though it may harm another non-native species, or do they seek alternative methods of control that may be less effective? From an ecological perspective, the decision to control invasivealiens is generally based on their impact on the native ecosystem. Invasivespecies are often characterized by their ability to outcompete native species for resources such as food, water, and space. This can lead to a decrease in biodiversity and disrupt ecological processes, ultimately leading to negative impacts on the ecosystem as a whole. As such, the primary goal of invasive species management is to mitigate these impacts and restore the balance of the ecosystem. However, when considering the potential harm to other non-native species, the decision becomes more complex. In some cases, the harm caused by invasive aliens may be so severe that it outweighs the potential harm to other non-native species. For example, if an invasive species is causing widespread destruction of native habitats and threatening the survival of native species, the priority may be to prioritize the control of the invasive species, even if it means some harm toother non-native species. This decision is often made based on the principles of conservation biology, which prioritize the protection of native biodiversity and the restoration of natural ecosystems. On the other hand, there are cases where the potential harm to other non-native species may be significant enough towarrant a reevaluation of invasive species management strategies. In these situations, conservationists and land managers may need to consider alternative methods of control that minimize the impact on non-native species while still effectively managing the invasive species. This could involve the use of targeted control methods that specifically target the invasive species, such as biological control agents or mechanical removal, rather than broad-spectrum methods that may harm a wider range of species. From a practical standpoint, the decision tocontrol invasive aliens while considering the potential harm to other non-native species requires a careful assessment of the risks and benefits of different management strategies. This assessment may involve conducting thorough ecological surveys to understand the potential impacts of different control methods on the local ecosystem, as well as considering the long-term implications of these decisions. It may also involve engaging with stakeholders, such as local communities and other interested parties, to ensure that their perspectives and concerns are taken into account. Ultimately, the decision to control invasive aliens while considering the potential harm to other non-native species is a complex and nuanced issue that requires a careful balancing of ecological, ethical, and practical considerations. While the protection of native biodiversity is a fundamental goal of invasive species management, it is important to recognize that the potential harm to other non-native species should also be taken into account. By carefully weighing the risks and benefits of different management strategiesand considering the perspectives of all stakeholders, conservationists and land managers can work towards effective and sustainable solutions for managinginvasive species while minimizing harm to other non-native species.。
InvasiveAlienSpecies:外来物种入侵
Policy Department A-Economy & Science Committee on the Environment, Public Health and Food Safety (ENVI)Invasive Alien SpeciesTuesday,17 December 2013-12:30-15:30European Parliament(Brussels),Altiero Spinelli (ASP) 1G 2The event is open to the public and will be web-streamed:http://www.europarl.europa.eu/ep-live/en/scheduleAgendaPart 1:Invasive alien species-What is at stake?12.30Welcome and introduction by the Chair,Pavel Poc,MEP, ENVI Rapporteur 12.40Invasive alien species: how do they arrive, and what are their impactsPiero Genovesi,ISPRA and Chair IUCN SSC Invasive Species Specialist Group12.50Prevention and management of the introduction and spread of invasive alienspecies-The Commission proposal for a regulationFrançois Wakenhut, Head of Unit Nature and Biodiversity,DG ENV 13.00State of play of discussions in CouncilInga Semeškaitė, Permanent representation of Lithuania to the EU 13.10Q&A, open discussionPart 2:Current experience and best practices13.25Introduction by Chris Davies,MEP, Draftsperson for the PECH committee13.30Gaining momentum: Status quo and trends of invasive alien species inEurope Franz Essl,Environment Agency Austria13.40Fighting IAS:better late than never but never late is betterBernardo Zilleti,GEIB(Grupo Especialista en Invasiones Biológicas,Spanishexpert group for biological invasions)13.50Managing Invasive Alien Species in the United KingdomNiall Moore,Non-native Species Secretariat UK14.00Eradication of alien plants: a matter of prompt reaction and resourcesinvested Jan Pergl,Institute of Botany and Academy of Sciences of the Czech Republic 14.10Q&A, open discussionPart 3:Priorities and challenges-Stakeholder Roundtable 14.25Introduction by Renate Sommer,MEP,ENVI Shadow Rapporteur 14.30Roundtable moderator:Wolfgang Rabitsch, Environment Agency AustriaEPO,European Pet Organization-Alex PloegFACE, Federation of Associations for Hunting&Conservation of the EU-C y Griffin CAB International-Richard ShawIUCN Office Brussels-Luc BasEPPO,European and Mediterranean Plant Protection Organization-Sarah BrunelThe European Botanical Gardens Consortium(invited)ELCA,European Landscape Contractors Association-Michael Henze 15.15Q&A, open discussion15.25Conclusions by the Chair。
外来物种入侵实施方案英文
外来物种入侵实施方案英文In recent years, the issue of invasive alien species has become a growing concern for many countries around the world. Invasive alien species, also known as non-native or exotic species, are plants, animals, or microorganisms that are introduced into a new environment where they are not native and have the potential to cause harm to the environment, economy, or human health.The impact of invasive alien species can be devastating. They can outcompete native species for resources, disrupt ecosystems, and even cause extinctions of native plants and animals. In addition, invasive alien species can also have significant economic impacts, such as reducing crop yields, damaging infrastructure, and increasing the cost of controlling their spread.To address the issue of invasive alien species, it is important to develop and implement effective management and control strategies. This requires a coordinated approach involving government agencies, non-governmental organizations, and the public. The following are some key components of an effective invasive alien species management plan:1. Prevention: The best way to manage invasive alien species is to prevent their introduction and establishment in the first place. This can be achieved through measures such as strict border controls, quarantine regulations, and public education and awareness campaigns.2. Early detection and rapid response: Invasive alien species can spread rapidly once they become established. Early detection and rapid response are essential to prevent their further spread and minimize their impact. This can be achieved through regular monitoring and surveillance, as well as the development of rapid response protocols.3. Control and eradication: Once invasive alien species have become established, it is important to implement control and eradication measures to minimize their impact. This may involve the use of physical, chemical, or biological control methods, as well as habitat restoration and reclamation efforts.4. Research and innovation: Invasive alien species management requires ongoing research and innovation to develop new and improved control methods, as well as to better understand thebiology and ecology of invasive species. This can help to inform management decisions and improve the effectiveness of control efforts.5. Collaboration and partnerships: Addressing the issue of invasive alien species requires collaboration and partnerships between government agencies, non-governmental organizations, research institutions, and the public. By working together, it is possible to develop and implement more effective management strategies.In conclusion, the issue of invasive alien species is a significant challenge that requires a coordinated and proactive approach. By developing and implementing effective management and control strategies, it is possible to minimize the impact of invasive alien species and protect native ecosystems, economies, and human health. It is essential to continue to work together to address this issue and prevent the further spread of invasive alien species.。
有害生物风险分析6 外来生物风险评估
评估前的准备
收集基础信息
明确拟评估对象
决定是否进行风险评估
收集基础信息
受外来物种影响区域的环境经济现状 外来物种的引进途径 外来物种的生物学特征 外来物种的管制状况 已有的外来物种风险评估情况 外来物种的危害
明确拟评估对象
外来入侵物种,需要评估其引进可能性、 建立自然种群可能性、扩散可能性和生态 危害 虽不能在当地建立自然种群或进行自然扩 散,但由于不适当的生产措施可能导致其 产生经济和环境危害的外来物种,只需要 评估其生态危害
原产地采取的有害生物管理措施(化学、生物、人工控制措施);
在原产地或运输和储存期间对货物采取的商业措施; 在原产地及我国常规口岸检疫中能否检出及其难易程度;
存储和运输条件以及运输的速度;
在运输和储存的过程中,该外来物种的存活能力和繁殖能力,生 活史及其长短; 针对有害生物的专门处理措施的有效性
中国第一批外来入侵物种名单
紫茎泽兰 薇甘菊 空心莲子草 豚草 毒麦 互花米草 飞机草 凤眼莲 假高梁
蔗扁蛾 湿地松粉蚧 强大小蠹 美国白蛾 非洲大蜗牛 福寿螺 牛蛙
中国第二批外来入侵物种名单
马缨丹 三裂叶豚草 大薸 加拿大一枝黄花 蒺藜草 银胶菊 黄顶菊 土荆芥 刺苋 落葵薯
逐步评估原则
外来入侵物种风险评估应按照识别风险、评估风险、管 理风险的步骤进行,根据具体情况逐步开展
工作程序
第一阶段进行评估前的准备,收集评估区域 基础信息,明确拟评估对象,决定是否进行 风险评估 第二阶段开展风险评估,分析发生入侵的可 能性及生态危害 第三阶段做出结论和建议,确定环境风险评 估的最终结果,判断环境风险是否可预测并 可接受,提出防控建议或替代方案。
外来物种调查实施方案英文
外来物种调查实施方案英文In recent years, the increasing number of invasive alien species has posed a serious threat to the ecological balance and biodiversity of many regions. In order to effectively manage and control these alien species, it is essential to implement a comprehensive and systematic investigation and management plan. This document outlines the implementation plan for an invasive alien species survey, aiming to provide guidance for researchers and management authorities.1. BackgroundInvasive alien species refer to non-native organisms that have been introduced to a new environment and have the potential to cause harm to the native ecosystem, economy, or human health. These species often outcompete native species, disrupt ecosystem functions, and result in significant economic losses. Therefore, it is crucial to conduct a thorough investigation of invasive alien species to understand their distribution, impact, and potential management strategies.2. ObjectivesThe primary objectives of the invasive alien species survey are:- To identify and document the presence of invasive alien species inthe target area- To assess the ecological and economic impact of invasive alien species- To develop management and control strategies for invasive alien species- To raise awareness and promote public engagement in invasive alien species management3. Survey MethodologyThe survey will utilize a combination of field surveys, remote sensing technology, and data analysis to achieve the objectives. The following steps will be undertaken:- Field Surveys: Trained personnel will conduct field surveys to identify and document the presence of invasive alien species. Data on species distribution, abundance, and habitat preferences will be collected.- Remote Sensing: Satellite imagery and GIS technology will be used to detect and monitor invasive alien species at a landscape scale. This will provide valuable information on the spatial distribution and spread of invasive species.- Data Analysis: The collected data will be analyzed to assess the ecological and economic impact of invasive alien species. This willhelp in prioritizing management actions and resource allocation.4. Management StrategiesBased on the survey findings, a range of management strategies will be developed to control and mitigate the impact of invasive alien species. These may include:- Mechanical and chemical control methods- Biological control using natural enemies of invasive species- Restoration of native habitats and ecosystems- Public awareness and education programs- Policy and regulatory measures to prevent further introductions5. Implementation and MonitoringThe survey findings and management strategies will be communicated to relevant stakeholders, including government agencies, non-governmental organizations, and the public. A monitoring program will be established to assess the effectiveness of management actions and to track changes in the distribution and impact of invasive alien species over time.In conclusion, the implementation of an invasive alien species survey is essential for understanding and managing the threat posed bythese species. By following the outlined methodology and strategies, we can work towards minimizing the impact of invasive alien species and preserving the ecological integrity of our natural environments.。
如何抵御物种入侵英语作文
如何抵御物种入侵英语作文Title: Combating Species Invasion。
In today's globalized world, the phenomenon of species invasion has become a pressing environmental issue. Species invasion, also known as biological invasion, refers to the introduction and spread of non-native species into new ecosystems, often resulting in negative ecological, economic, and social consequences. Effectively combating species invasion requires a multifaceted approach involving prevention, early detection, rapid response, and management strategies. In this essay, we will explore various methods to combat species invasion.First and foremost, prevention is key to mitigating the spread of invasive species. This involves implementing stringent biosecurity measures at borders and ports to prevent the unintentional introduction of invasive species through trade and travel. Additionally, raising public awareness about the dangers of species invasion andencouraging responsible consumer choices can help prevent the intentional introduction of invasive species, such as through the release of exotic pets or aquarium plants into the wild.Early detection is crucial for promptly identifying and responding to invasive species before they become established and widespread. Utilizing advanced technologies such as remote sensing, DNA analysis, and citizen science initiatives can aid in the early detection of invasive species. Furthermore, establishing comprehensive monitoring programs to regularly survey vulnerable ecosystems can help detect invasive species at their earliest stages of establishment.Once invasive species are detected, a rapid response is necessary to prevent further spread and minimize ecological damage. This may involve employing various eradication and control methods tailored to the specific characteristics of the invasive species and the affected ecosystem. Some common control measures include mechanical removal, chemical treatments, biological control using naturalpredators or pathogens, and habitat restoration efforts to enhance the resilience of native species.In addition to prevention and rapid response, long-term management strategies are essential for effectively managing established invasive species and restoring native biodiversity. Integrated pest management approaches that combine multiple control methods while minimizing environmental impacts are often employed for sustainable invasive species management. Furthermore, fostering collaboration among government agencies, research institutions, NGOs, and local communities is vital for implementing coordinated management plans and sharing knowledge and resources.Education and outreach initiatives play a crucial role in engaging stakeholders and empowering communities to take action against species invasion. By educating the public about the ecological impacts of invasive species and providing guidance on how individuals can contribute to prevention and management efforts, we can foster a sense of environmental stewardship and collective responsibility.In conclusion, combating species invasion requires a comprehensive and coordinated approach that encompasses prevention, early detection, rapid response, and long-term management strategies. By implementing stringentbiosecurity measures, enhancing monitoring and detection capabilities, employing effective control methods, and fostering collaboration among stakeholders, we can minimize the ecological, economic, and social impacts of invasive species and safeguard native biodiversity for future generations.。
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This document will not be distributed at the meeting. Please bring this copy.Ce document ne sera plus distribué en réunion. Prière de vous munir de cet exemplaire.Strasbourg,5th December 2003T-PVS (2003) 7 revised[tpvs07erev_2003]CONVENTION ON THE CONSERVATION OF EUROPEAN WILDLIFEAND NATURAL HABITATSStanding Committee23rdmeetingStrasbourg, 1-5 December 2003__________European StrategyonInvasive Alien SpeciesFinal VersionDocument prepared byMr Piero Genovesi and Mrs Clare ShineT-PVS (2003) 7 revised - 2 –T ABLE OF CONTENTSINTRODUCTION (4)Why are invasive alien species a problem? (4)IAS status and trends in Europe (4)International action on invasive alien species (5)Rationale for a European Strategy on Invasive Alien Species (5)Challenges and opportunities for the Strategy (6)Who is the strategy for? (6)Abbreviations (7)STRATEGY (8)Objectives (8)Scope (8)Terminology (9)1. Building awareness and support (10)2.Collecting, managing and sharing information (11)2.1 Species inventories (11)2.2 Research and monitoring (12)2.3 Regional exchange of information (13)3.Strengthening national policy, legal and institutional frameworks (14)3.1 Leadership and coordination (15)3.2 Policy and legal review and development (16)3.3 Strategies and action plans (17)3.4 Key approaches and tools (18)3.5 Ancient introductions (20)3.6 Compliance and enforcement (21)4.Regional cooperation and responsibility (22)4.1 Cooperation between Bern Convention Parties (22)4.2 Role of the Bern Convention (23)4.3 Subregional cooperation (24)5. Prevention (25)5.1 Prevention at source and on arrival: border control and quarantine measures (26)5.2 Intentional introductions (27)5.3 Unintentional introductions (28)5.4 In-country prevention (30)5.5 Special measures for isolated ecosystems (31)5.6 Prediction and prevention of spontaneous spread (31)6.Early detection and rapid response (32)6.1 Surveillance (32)6.2 Rapid response and contingency planning (33)7.Mitigation of impacts (34)7.1 Policy and legal aspects (35)7.2 Eradication (36)7.3 Containment (38)7.4 Control (39)8.Restoration of native biodiversity (40)- 3 – T-PVS (2003) 7 revised The authors wish to thank Ana Isabel Queiroz (Institute for Nature Conservation, Portugal) for her stimulating and very valuable intellectual contribution throughout the preparation of the Strategy. The authors are also grateful to the Governments of Switzerland and Belgium, whose voluntary financial contributions made the production of this Strategy possible.T-PVS (2003) 7 revised - 4 –I NTRODUCTIONWhy are invasive alien species a problem?The introduction of species beyond their natural range is rising sharply, due to increased transport, trade, travel and tourism and the unprecedented accessibility of goods resulting from globalisation. These activities provide vectors and pathways for live plants, animals and biological material to cross biogeographical barriers that would usually block their way.Most alien species do not become invasive or cause problems in their new locations: many have considerable benefits to society e.g. in agriculture, horticulture, forestry and the pet industry. However, the subset of alien species that are invasive can have significant environmental, economic and public health impacts and present a significant risk of the wholesale homogenisation of ecosystems.Invasive alien species (IAS) are now considered to be the second cause of global biodiversity loss after direct habitat destruction and have adverse environmental, economic and social impacts from the local level upwards. The European Community has recognized proliferation of IAS as an emerging issue1, noting that IAS introductions are one of the main recorded causes of biodiversity loss and cause serious damage to economy and health.2IAS status and trends in EuropeIntroductions in Europe and the Mediterranean basin started in ancient times. In some cases, the impacts on native ecosystems occurred so long ago that we hardly perceive the effects on the biodiversity of the region. But although the history of species introductions in Europe is very ancient, the phenomenon has grown rapidly and enormously in recent times as a result of increasing globalisation. In addition, climate change affects the abundance and spread of IAS and the vulnerability of ecosystems to invasions. IAS are now a major challenge for biodiversity conservation in Europe in the new millennium. Several endangered species in Europe are threatened by IAS (e.g. European mink by the American mink3; White-headed duck by the Ruddy duck4). The ongoing expansion of the American grey squirrel in north-west Italy is causing the progressive disappearance of the native red squirrel in all overlap areas and is considered a potential threat to forest ecosystems at a continental scale5. European forests have been profoundly altered by Dutch elm disease, caused by fungi introduced from Asia, that devastated elm tree populations in much of central Europe and Great Britain6.European island biotas, hosting a major portion of the region’s biodiversity, are particularly vulnerable to invasions because increased travel and trade break down the natural barriers that have protected and forged these biotas in million years. As a result, the number of invasive alien species on European islands is increasing exponentially and has led to an unprecedented extinction crisis of the islands' endemic species.As well as damaging biodiversity, IAS have also imposed huge losses on the European economy. Introduced pests and diseases affect agriculture and forestry and alien parasites (such as Gyrodactylus salaris and Anguillicola crassus) have led to dramatic decreases in fisheries sector incomes in several Nordic States7. The muskrat and coypu, both introduced in the last century by the European fur industry,1 COM(2001)162 final.2 European Council (Environment), Conclusions of 4 March 2002: 6592/02 (Presse 47 - G) 24.3Sidorovich V, Kruuk H & Macdonald DW (1999) Body size, and interactions between European and American mink (Mustela lutreola and M. vison) in Eastern Europe. Journal of Zoology 248: 521-5274 Hughes B, Criado J, Dalany S, Gallo-Orsi U, Green A, Grussu M, Perennou C & Torres JA (1999) The status of the ruddy duck (Oxyura jamaicensis) in the western Palearctic: towards an action plan for eradication. Report by the Wildlfowl & Wetlands Trust to the Council of Europe5 Bertolino S., P. Genovesi, 2003. Spread and attempted eradication of the grey squirrel (Sciurus carolinensis) in Italy, and consequences for the red squirrel (Sciurus vulgaris) in Eurasia. Biological Conservation, 19: 351-358.6 Schrader G., J.G. Unger (2000). Plant pests as alien invasive species: success and failure of European phytosanitary measures – a German view. CBD Technical Series n°1: 81-83.7 Weidema I (ed) (2000) Introduced Species in the Nordic Countries. Nord 2000:13. Nordic Council of Ministers, Copenhagen- 5 – T-PVS (2003) 7 revised damage river banks through digging and have increased the risk and severity of floods in many central and southern European States. The introduction of the American comb jelly (Mnemiopsis leidyi) into the Black and Azov Seas, caused the near extinction of the anchovy and sprat fisheries8.International action on invasive alien speciesBecause IAS are a global problem, unilateral action by a few States can never be enough to prevent unwanted introductions. Cooperation at international, regional, transboundary and local levels is essential to develop compatible approaches to common problems.Many international instruments or technical guidelines already deal with IAS issues from various perspectives: plant and animal health, biodiversity conservation, aquatic ecosystems, some sectoral pathways (a summary of key instruments is provided in the Annex to the Strategy). These binding or voluntary instruments provide the baseline from which States and regional economic integration organizations such as the European Community develop policy, legal and management frameworks to address IAS issues.In recent years, IAS have become a high-profile policy topic for the international community which has emphasised the need for cross-sectoral coordination between competent institutions and stakeholders at all levels. New programmes and tools have been developed, notably the Global Invasive Species Programme (GISP)9 which actively promotes practical regional cooperation. GISP has published a Global Strategy on Invasive Alien Species and a Toolkit of Best Prevention and Management Practices10. The Convention on Biological Diversity (CBD) has identified IAS as a major cross-cutting theme. This global treaty requires Parties “as far as possible and as appropriate, (to) prevent the introduction of, control or eradicate those alien species which threaten ecosystems, habitats or species” (Article 8(h)). In 2002, the CBD Conference of the Parties adopted a specific Decision and Guiding Principles11 to help Parties implement this requirement. The Decision urges Parties, other governments and relevant organizations to prioritise the development of IAS strategies and action plans at national and regional level and to promote and implement the CBD Guiding Principles.The CBD Guiding Principles set out a “Three-stage hierarchical approach” as the basis for all action on IAS:•prevention of IAS introductions between and within States is generally far more cost-effective and environmentally desirable than measures taken after IAS introduction and establishment;•if an IAS has been introduced, early detection and rapid action are crucial to prevent its establishment: the preferred response is often to eradicate the organisms as soon as possible;•where eradication is not feasible or resources are not available, containment and long-term control measures should be implemented (CBD Guiding Principle 2).However, it is important to go further than this basically defensive approach. Conservation policies need to include restoration measures for species, natural habitats and ecosystems that have been affected by biological invasions.Rationale for a European Strategy on Invasive Alien SpeciesEurope is a major trading bloc with many contiguous States and shared borders and highly-developed free trade arrangements. Huge volumes of species are translocated, intentionally and unintentionally, in8 Ivanov V.P., Kamakin A.M., Ushivtzev V.B., Shiganova T. A., Zhukova O., Aladin N., Wilson S.I, Harbison R and Dumont H.J. (2000) Invasion of the Caspian Sea by the Comb Jellyfish Mnemiopsis leidyi (Ctenophora). Biological Invasions 2: 255-258.9 GISP is an international network of volunteers from various backgrounds: scientists, economists, lawyers, policy makers, activists and others from all sectors and constituencies affected by IAS. It has three partners: IUCN-The World Conservation Union; the intergovernmental bioscience organisation CAB International; and the Scientific Committee on Problems of the Environment (SCOPE).10 McNeely et al (2001) Global Strategy on Invasive Alien Species. IUCN; Wittenberg and Cock (2001) Invasive Alien Species: A Toolkit of Best Prevention and Management Practices. GISP/CAB International.11 Decision VI/23 on Alien Species that threaten ecosystems, habitats and species (COPVI, The Hague, April 2002) to which are annexed the Guiding Principles for the Prevention, Introduction and Mitigation of Impacts of Alien Species that threaten Ecosystems, Habitats or Species.T-PVS (2003) 7 revised - 6 –the course of routine sectoral activities between and within States. Potentially invasive alien species may easily reach neighbouring States or ecologically different parts of the same State.The need for a regional approach has long been recognised by European institutions such as the Convention on the Conservation of European Wildlife and Natural Resources 1979 (Bern Convention), the European and Mediterranean Plant Protection Organisation (EPPO) and the European Community, which have all developed legal and technical references for different aspects of IAS (see Annex to the Strategy).The Bern Convention, to which the European Community and 38 European states are party, requires Parties “to strictly control the introduction of non-native species” (Article 11.2.b). Since 1984, a range of actions have been initiated for more effective implementation of this article. These include the adoption of Standing Committee recommendations on general IAS issues and specific problems, production of technical reports, organisation of workshops and establishment of an IAS Experts’ Group.Despite these and other efforts, Europe now lags behind other regions that have developed strategic frameworks to address IAS in a holistic way. Whilst Europe’s complex characteristics can make it harder to develop and implement common trade and movement policies, this should not be used to postpone decisive and balanced action. The common trade and movement policy for the plant health sector developed under EPPO shows that coordination and cooperation is feasible.The impacts of many past invasions could have been reduced if European States had uniformly applied appropriate best practices and taken rapid action to eradicate introduced species following detection. Most biological invasions now threatening Europe might have been prevented by greater awareness of IAS issues and a stronger commitment to address them.Current inaction in many - though not all - States and sectors may threaten the region’s biodiversity, public health and economic interests. In line with international policy, it is now essential to develop efficient cooperation at national and regional level to prevent or minimise adverse impacts of IAS.The Bern Convention initiative for a European Strategy on Invasive Alien Species, in collaboration with the European Section of the IUCN Invasive Species Specialist Group, began in 2000. It has been welcomed by the Second Intergovernmental Conference on Biodiversity in Europe in Budapest and the CBD.Challenges and opportunities for the StrategyMany European States face similar constraints in their IAS efforts. Depending on the country, these may include:•low public awareness and opposition to government intervention;•shortage and inaccessibility of scientific information (for species identification, risk analysis, detection and mitigation techniques etc.);•absence of clear and agreed priorities for action;•ease of introduction and movement (e.g. through the post), inadequate inspection and quarantine;•inadequate monitoring capacity;•lack of effective emergency response measures;•outdated or inadequate legislation;•poor coordination between government agencies, States and other stakeholders.The Strategy addresses these constraints. It aims to facilitate implementation of international commitments and best practice and to support development of realistic policies, measures and targets. Priority actions are proposed that are key in terms of time and feasibility of implementation.The Strategy recognizes that Parties’ existing legal obligations may constrain or influence the measures which can be taken, particularly with regard to regulation of trade-related activities.Who is the Strategy for?The Strategy is primarily targeted at governments of Contracting Parties to the Bern Convention and of other European States. It is a comprehensive document addressed to nature conservation agencies and all- 7 – T-PVS (2003) 7 revised other sectoral agencies with responsibility for activities relevant to IAS prevention or management. It isrecognised that many aspects of implementation will be delivered through existing plant, animal andhuman health agencies which have long-standing expertise in particular areas (e.g. micro-organisms). The Strategy is also addressed to the Bern Convention Secretariat and strongly supports closer and sustained coordination and cooperation with relevant European and international organisations. Although the Strategy is mainly intended to address IAS problems in Europe, it also applies to African States that are Parties to the Convention, as the principles and actions proposed should help to prevent unwanted introductions and mitigate the impacts of IAS in those States.The Strategy also seeks to engage stakeholders involved in the movement, use and control of potentially invasive alien species (industry and trade, transporters, retailers, resource managers, the public etc.) and to build on the expertise and commitment of competent non-governmental organisations and research institutes. Many of the proposed key actions call for joint or complementary initiatives by private and public stakeholders.A BBREVIATIONSBern Convention Convention on the Conservation of European Wildlife and Natural Resources CBD Convention on Biological DiversityCBD Guiding Principles Guiding Principles for the prevention, introduction and mitigation of impactsof alien species that threaten ecosystems, habitats or species (annexed toDecision VI/23 adopted by the Conference of the Parties to the CBD, TheHague, April 2002)CMS Convention on the Conservation of Migratory Species of Wild AnimalsimpactassessmentEIA EnvironmentalEPPO European and Mediterranean Plant Protection OrganisationGISP Global Invasive Species ProgrammespeciesalienIAS InvasiveIPPC International Plant Protection Convention 1951, revised 1997IMO International Maritime OrganisationCommission’s Invasive Species Specialist GroupSurvivalSpeciesISSG IUCNUnionIUCN WorldConservationorganisationNGO Non-governmentalRamsar Convention on Wetlands of International Importance especially as WaterfowlHabitatOIE Office international des epizooties (World Organisation for Animal Health) SEA StrategicassessmentenvironmentalWTO-SPS World Trade Organization Agreement on the Application of Sanitary andPhytosanitary Measures (1995)T-PVS (2003) 7 revised - 8 –S TRATEGYObjectivesThe Strategy promotes the development and implementation of coordinated measures and cooperative efforts throughout Europe to prevent or minimise adverse impacts of invasive alien species (IAS) on Europe’s biodiversity, as well as their consequences for the economy and human health and well-being. The Strategy provides guidance to help Bern Convention Parties in their efforts to:•rapidly increase awareness and information on IAS issues and ways to tackle them (§1-2);•strengthen national and regional capacity and cooperation to deal with IAS issues (§3-4)•prevent the introduction of new invasive alien species into and within Europe (§5) and support rapid response to detected incursions (§6);•reduce the adverse impact of existing invasive alien species (§7);•recover species and restore natural habitats and ecosystems that have been adversely affected by biological invasions, where feasible and desirable (§8); and•identify and prioritise key actions to be implemented at the national and regional level.ScopeThe Strategy covers:•terrestrial, freshwater and marine environments under the sovereignty or jurisdiction of Bern Convention Parties. It also provides guidance for activities carried out in areas beyond national jurisdiction (e.g. shipping);•alien species (as defined by the Conference of the Parties to the Convention on Biological Diversity: see Box 1) in all taxonomic groups, including viruses, prions, bacteria mycorrhiza and feral animals of domestic species (cats, dogs, goats, etc.).It does not apply to genetically modified organisms12.12 The Strategy does not cover genetically modified organisms/living modified organisms, although some of these have the potential to become IAS, because these are separately regulated under European Community legislation and by several other European states. However, there may be scope for countries to coordinate activities relevant to both IAS and genetically modified organisms (e.g. risk analysis, contained use, field trials, control of release, monitoring).- 9 – T-PVS (2003) 7 revised Terminologyof the Parties to the Convention on Biological Diversityfor the purposes of the CBD Guiding Principles (see Box1).For plant health and animal health issues, internationally-agreed terminology developed by competent organisations(IPPC, OIE) is relevant.For the purposes of this Strategy:“regional” refers to the whole of Europe;“subregional” refers to an area (land, sea or freshwater)shared by two or more neighbouring States.“pathway” means, as applicable:•the geographic route by which a species movesoutside its natural range (past or present);•the corridor of introduction (e.g. road, canal,tunnel); and/or•the human activity that gives rise to an intentionalor unintentional introduction.“vector” means the physical means or agent (i.e. aeroplane,ship) in or on which a species moves outside its naturalrange (past or present).T-PVS (2003) 7 revised - 10 –1. Building awareness and supportCBD Guiding Principle 6: Education and public awarenessIn Europe, both the public and decision-makers often have limited understanding of the range of threats posed by IAS. This can make it hard to mobilise relevant agencies and other stakeholders, particularly for introductions that do not affect human health or major economic interests. Raising awareness and commitment is essential to develop shared responsibility and to encourage private efforts and voluntary compliance.AimEurope’s public, decision-makers, scientists and other stakeholders have high awareness of IAS risks and the benefits of IAS prevention and mitigation for native biodiversity, the economy and human health and wellbeing. Stakeholders are actively engaged in the development of best practices to prevent IAS impacts.Key actions1.1Set up vigorous information and education programmesfor different target audiences (general public, schools,local authorities, government agencies etc.).1.2Incorporate IAS into existing education and publicawareness programmes where appropriate, (e..g. onnative species and habitat conservation, protected areas,wildlife trade).1.3Work with key stakeholders to produce and disseminateusing or affected by IAS (see Box 2 and Boxes 16-17).1.4Support the holding of workshops and conferences onIAS.- 11 – T-PVS (2003) 7 revised2. Collecting, managing and sharinginformationNational and regional capacity to identify, prevent andmitigate IAS threats depends on accurate and updatedinformation that is easily accessible.Information-sharing between States is critical: answersto a problem may be available elsewhere in Europe or theworld. There is currently no pan-European informationmechanism on IAS as such, although important resourcesexist for some taxonomic groups and in some sectors (e.g.the EPPO/EC plant health system). Information gaps(biologic, taxonomic, geographic) can make it harder todetermine priorities and take effective prevention andresponse measures. Array 2.1. Species inventoriesCBD Guiding Principle 8.1: Exchange of informationAimA clear understanding of alien species established onnational territory is developed to help identify species thatare invasive, set priorities for research, prevention,monitoring and mitigation and rapidly detect new arrivalsnot already present in the country or part of the country .Key actions2.1.1 Develop a national inventory of alien species inrelevant taxonomic groups recorded in the wild innational territory, giving priority to IAS and usingexisting data formats, standards and protocols whereverpossible (see Box 3). Regularly update the inventory toinclude newly-detected alien species,.2.1.2 Create and regularly update alien species pages in thenational biodiversity Clearing House Mechanism orequivalent and link these to relevant European andglobal IAS information networks to ensure rapiddissemination of information (see §2.3).T-PVS (2003) 7 revised - 12 –2.2.Research and monitoringCBD Guiding Principles 5: Research and monitoringCBD Guiding Principle 9.d: Cooperation including capacity buildingAimsThrough systematic monitoring, the ecology, distribution, patterns of spread and response to management of IAS are better understood.Capacity to predict the consequences of alien species introductions is strengthened.Critical information is available to support IAS prevention, mitigation and restoration programmes and provide a stronger scientific basis for decision-making and allocation of resources.Key actions Array 2.2.1 Support research on priority topics (see Box 4).2.2.2 Review existing research and monitoring programmesto identify gaps, areas for development andopportunities for more effective collaboration withinEurope.2.2.3 As necessary, establish or expand monitoring systemsfor pathways, vectors and vulnerable points (see §6).- 13 – T-PVS (2003) 7 revised2.3. Regional exchange of informationCBD Guiding Principle 4.3: The role of StatesCBD Guiding Principle 8.1: Exchange of informationCBD Guiding Principle 9.a: Cooperation, including capacity-buildingAimsEffective systems are in place to share IAS informationwith neighbouring countries, trading partners and regionswith similar ecosystems to facilitate identification, earlywarning and coordination of prevention, mitigation andrestoration measures.Information systems can locate, document and provideelectronic access to sources of information, provide qualitycontrol and ensure controlled vocabularies. Common dataprotocols or standards are used where possible. Array Key actions2.3.1 Identify and assist lead organisations (e.g. IUCNInvasive Species Specialist Group, European TopicCentre for Nature Protection and Biodiversity) todevelop an interlinked European information networkon IAS, using existing information resources andcapacity as far as possible (see Box 5).2.3.2 Draw up and link registers of European experts andinstitutions that can advise on taxonomy and othertechnical IAS issues.2.3.3 Promote regular meetings and workshops to updateinformation on taxonomy, biology, ecology,epidemiology, methods of mitigation and restoration(see also §1.3).T-PVS (2003) 7 revised - 14 –3. Strengthening national policy, legal andinstitutional frameworksInvasive alien species - as a cross-cutting issue – concern many social, economic and environmental interests, including trade, health, agriculture, forestry, water resource management, infrastructure development, horticulture, aquaculture, tourism and recreation. In most countries, several departments and agencies have responsibility for some aspect of IAS prevention and management and several different laws may be relevant (e.g. plant and animal health and quarantine; hunting and fishing; nature conservation etc.).The result can be a complex situation where responsibilities, policies and laws are not very clear or even compatible. This can also hamper efficient communication within the region.It is therefore crucial that Parties initiate a coordinated review process of their institutional and legal frameworks and their strategies, policies and approaches relevant to IAS issues.In several European States, responsibility for environmental policy and nature conservation issues is decentralised to subnational authorities. The Strategy recommends that IAS issues are addressed (or at least coordinated) at the national level, but recognises that each country will need to chose an appropriate structure or network for this purpose.。