浅议我国外来物种入侵问题及其防治对策

随着世界经济的发展和全球经济一体化进程的加快,外来物种入侵已成为影响国家安全的主要因素之一。我国外来入侵物种数量繁多,已成为遭受外来生物危害最严重的国家之一,入侵物种已对我国生态系统、环境和社会经济造成了严重的影响。近年来,各国都积极采取措施,制定外来物种入侵管理政策,加强外来物种入侵立法,确保国家及国际生物安全。然而,我国现有的针对外来物种的相关法律法规存在明显滞后。本文综述了我国外来物种入侵的现状及相关立法,指出外来物种入侵可在不同生态系之间发生,揭示了行政区划与生态系差异造成外来物种入侵管理存在"自然与经济的错位"、国内管理方面存在"生态系统与行政区域的错位"的"双错位现象",分析了我国外来物种的管理现状及今后的发展方向,以期探求我国在国际背景下的外来物种管理对策,提出制定《外来入侵物种法》及相关法律的国家体系、建立跨部门协作科学研究体系以及建设行政管理体系,增强抵御外来物种入侵的能力,实施以防为主的管理策略。     

维护我国生态安全,防范外来物种入侵的几点思考

随着全球经济一体化,国际贸易和旅游业的快速发展,外来物种入侵现象日益加剧,对我国生态安全和生物多样性保护构成了极大的威胁,加强外来入侵物种的防范和管理已迫在眉睫。本文分析了我国外来物种入侵的途径、入侵特征以及外来入侵物种对我国造成的危害,探讨了防范外来入侵物种的对策。     

我国外来入侵生物防控现状、问题和对策

外来物种入侵已经威胁全球多个国家和地区,严重影响农林牧渔业生产,威胁生态系统稳定,是当前全球生物多样性丧失的主要原因之一,开展入侵物种防控已成为生物多样性保护与农业绿色发展的重点工作。我国已经成为全球遭受生物入侵威胁与损失最为严重的国家之一,截至2018年底,入侵我国的外来物种有近800种,已确认入侵农林生态系统的有638种,全国31个省（区、市）均有外来生物入侵发生并带来危害,半数以上县域都有入侵物种分布,几乎涉及所有类型的生态系统。本文对全球主要发达国家外来入侵物种发生情况及防控进行梳理发现,从国家层面立法开展外来入侵生物防控成为主流,制定长期防控战略并增加投入是入侵物种防控成功的关键。近些年,我国在外来入侵物种防控方面初步建立了工作机制,发布了重点管理外来入侵物种名录,完成了重点入侵物种的调查监测,开展了局部地区的防控措施,积极推动立法工作。根据国外生物入侵防治经验与我国实际情况,本研究提出我国外来入侵物种防控对策建议,包括加强法制建设、开展本底调查和启动重大防控工程等,为我国外来侵入生物的防控提供借鉴。     

我国部分国家级自然保护区外来入侵物种的分布概况

基于我国53 个国家级自然保护区外来入侵植物调查与24 个国家级自然保护区外来入侵动物调查数据, 分析了外来入侵物种种类、分布状况等。调查共发现外来入侵物种201 种, 包括入侵植物176 种和入侵动物25 种。52.08%的外来入侵植物已入侵到我国国家级自然保护区, 30 个国家级自然保护区受外来入侵物种影响显著, 52 个国家级自然保护区分布有环保部公布的外来物种。云南纳板河流域国家级自然保护区外来入侵物种数目最多, 为61 种; 小蓬草(Erigeron canadwnsis)在国家级自然保护区中的出现频率最高, 为0.736。外来入侵物种已严重威胁我国自然保护区的生态安全, 亟需对保护区的外来入侵物种采取相应的防控措施, 推进外来入侵物种管理成为保护区管理工作的基本内容。     

海洋外来物种入侵生态学研究

海洋外来物种入侵已成为最为严重的全球性环境问题之一。海洋生态系统类型多样、环境复杂,其生物入侵的监测、控制与管理难度相对较大。我国对陆地外来生物的入侵已开展了较为深入的研究,但对于海洋外来生物的入侵研究仍处于起步阶段,对其入侵监测、入侵机制、入侵危害的程度以及防治等问题缺乏基础数据。本文在分析国内外海洋外来生物入侵现状的基础上,概述其入侵生态学研究形势及相关成果,包括海洋外来物种的入侵途径、入侵过程、入侵生态效应以及全球变化对入侵的影响等。海洋外来生物的入侵可能对海洋生态系统造成直接或间接的影响,如种间竞争破坏生态环境、与土著种杂交造成遗传污染、病原生物及有毒藻类导致海洋生态灾害加剧等。此外,从政策和法规、入侵风险评估、监测和公共宣传教育、生物信息系统和有效管理机制等方面提出对我国海洋外来物种入侵的防治策略。本研究为我国海洋外来物种的进一步研究提供了参考。     

影响河北省外来物种入侵的社会经济因素分析

【目的】探讨影响河北省外来物种入侵的社会经济因素,以期能够为河北省外来物种的防控提供可行性建议对策。【方法】通过查阅期刊、专著和数据库等分析了河北省外来入侵物种情况,对2003、2007、2011、2015、2019年5个时间节点的进口贸易、旅游人数、境内公路公里数3个社会经济变量与外来入侵物种量进行相关性分析,明确影响河北省外来入侵生物的社会经济因素,进而通过建立时间序列模型预测出未来几年进口贸易额的变化情况,利用曲线估计预测2023年的外来入侵物种数量。【结果】河北省外来入侵物种数呈现逐年增长的趋势,且在各年的外来入侵物种中均有超过85%是与人类活动有关;进口贸易总额、入境旅游总人数和境内公路公里数与外来入侵物种数之间都表现出显著的正相关关系;预测显示,到2023年河北省的外来入侵物种数将达到367种。【结论】社会经济的发展将会带来更多的外来入侵物种,基于河北省外来入侵生物的入侵途径提出了防控外来物种入侵的对策。     

外来入侵物种管理中的排序体系研究进展

外来物种入侵是继生境破坏之后的第二大世界性的环境问题, 如何实现外来入侵物种分级, 对其进行有效管理是一个世界性的难题。研究总结了国内外外来入侵物种的排序体系, 从三个方面归纳了目前的排序系统: 1)针对所有入侵以及潜在入侵物种开展综合风险评估, 以此为基础提出防控管理清单; 2)针对已建群的外来入侵物种, 围绕不同管理目标进行入侵物种的排序, 包括以降低外来入侵物种对生物多样性影响为目的的外来植物排序、以生物防治为控制手段的外来物种排序、基于土地利用的种群管理排序; 3)针对区域管理提出外来入侵物种分区管理。认为外来入侵物种的入侵性、生态危害、分布范围、潜在分布和控制技术是实现排序的关键因素, 指标的选择与确定依赖于管理目标的设定。我国亟需确定外来入侵物种的优先控制区域, 并针对不同优先控制区域内外来入侵物种开展排序工作。     

澳大利亚外来入侵物种管理策略及对我国的借鉴意义

澳大利亚是一个岛状大陆,海洋运输业十分发达,通过贸易、旅游、运输等途径有意或无意引进有害外来物种的风险较大。澳大利亚政府高度重视外来入侵物种的管理工作,制定了《澳大利亚国家生物多样性保护策略》,针对外来杂草和通过压舱水载入的海洋外来入侵物种的管理制定了《国家杂草策略》、《杂草风险评价系统》和《压舱水指南》等法规和技术性文件,加强了对外来入侵物种的管理。本文简要介绍了澳大利亚外来入侵物种管理的有关策略和指南,并提出了我国在外来入侵物种管理方面的对策建议：（1）尽快建立相应的法规体系,实现外来入侵物种的依法管理;（2）加强机构建设,形成多部门的协调管理机制;（3）加强外来入侵物种管理制度的建设;（4）采取适当的引进预防、消除、控制和恢复措施;（5）开展科学研究,为外来入侵物种的管理提供科学依据;（6）制定教育和培训计划,提高公众意识。     

中国外来入侵生物的空间分布格局及其影响因素

不同地理区域影响生物分布格局的因子不同,对外来入侵物种也是如此。在区域尺度上分析外来入侵生物的空间分布格局及其影响因子对预测生物入侵的影响及入侵种的控制管理具有重要意义。本研究应用中国外来入侵物种数据库、自然环境数据库和社会人文环境数据库,分析了我国外来入侵动植物的空间格局;并运用主成分分析（PCA）和典范对应分析（CCA）探讨了自然环境和人类活动等因素对外来入侵动植物分布格局的影响;同时研究了外来入侵物种多样性与本地物种多样性之间的关系。结果表明,我国现有外来入侵动物138种、入侵植物384种,其数量和密度都呈现出由东南沿海向西北内陆减少的趋势,且入侵动物和入侵植物空间格局基本一致;降水（MAP）是决定我国外来入侵动植物分布格局的主要自然环境因子,国民生产总值（GDP）是主要社会经济影响因子。在全国尺度上,外来入侵物种多样性与本地物种多样性之间呈显著的正相关关系,但地域间存在较大差异。不同区域外来入侵物种与本土物种多样性的相关关系表现出不同,与研究尺度有密切关系。     

“世界100种恶性外来入侵物种”在我国大陆的入侵现状

[目的] 明确世界自然保护联盟公布的“世界100种恶性外来入侵物种”在我国大陆发生分布现状,为我国制定外来入侵物种管控对象和分级管理对策提供依据。[方法] 基于在线数据库系统、文献报道以及外来入侵物种本底调查结果,采用分类统计方法,对物种的分类地位、原产地、在我国的入侵状态及其所在的生态系统进行分析。[结果] 世界100种恶性外来入侵物种已有82种在我国发生分布,包括本地种33种、外来入侵种32种、外来非入侵种16种,以及未明确入侵状态1种。其中,32种外来入侵种包括陆生无脊椎动物8种、哺乳动物2种、鱼类2种、两栖动物1种、爬行动物1种、水生无脊椎动物2种、陆生植物9种、水生植物4种、真菌1种、卵菌1种和病毒1种。以上物种主要分布在东南沿海地区和西南地区,而较少分布在西北地区和东北地区;约75%物种分布在农田、城镇、森林和湿地4类生态系统。[结论] 建议外来入侵物种管理部门重点关注尚未在国内发生分布的18种潜在外来入侵物种,并列入国家外来入侵物种相关管理对象,严防其传入与扩散;严密监控国内已发生且具有潜在危险的外来物种,防止其向可能入侵的生态系统边缘扩散;继续对在国内已发生的外来入侵种实施区域性分级控制管理措施。     

近年来中国热带地区外来有害昆虫的种类特征及入侵分析

我国热带地区是外来入侵物种发生与危害的重灾区,近年来外来有害昆虫入侵所引发的生物灾害及生态安全问题日趋严峻。在海南省、广东省、广西壮族自治区、云南省、福建省外来入侵昆虫的调查结果及文献资料的基础上,整理分析了中国热带地区外来入侵昆虫的种类构成、分布、原产地及首次发现地。据统计,2000-2014年我国热带地区的外来入侵昆虫种类共计23种,隶属于6目11科,数量最多的为半翅目(13种,56.52%),其中以粉蚧科和粉虱科居多;热带地区的外来入侵昆虫在不同地区之间的物种数量差异较大,其中海南省最多(19种,82.61%),其后依次为广东省(16种,69.57%)、云南省(14种,60.87%)、广西壮族自治区(12种,52.17%),而福建省最少(9种,占39.13%);在入侵我国热带地区的外来有害昆虫中,原产于亚洲、北美洲的种类最多均为6种,占26.09%,南美洲占21.74%,而从非洲、大洋洲、欧洲传入的分别占8.70%、4.35%、4.35%;外来入侵昆虫的首次发现地位于广东省的有9种,占39.13%,出现在海南省和云南省的各占30.43%、21.74%,出现在广西壮族自治区的为8.70%。阐明我国热带地区外来有害昆虫的种类特征及入侵现状,可为该地区外来入侵昆虫的监测与防控提供一定的依据。     

福建省农田生态系统外来入侵植物种类及其分布

为掌握福建省农田生态系统的外来入侵植物种类和分布情况,采用实地调查的方式,对福建省9市农田生态系统中的入侵植物进行调查,并分析了其种类组成、原产地、生活型、分布格局和分布类型及其入侵性等。结果表明,福建省农田生态系统有外来入侵植物30科65属共79种;其中以菊科（Asteraceae）物种数最多,为22种,占总种数的27.85%,其次是苋科（Amaranthaceae）有7种,豆科（Leguminosae）、禾本科（Gramineae）、旋花科（Convolvulaceae）和大戟科（Euphorbiaceae）各有5种。生活型以草本植物为主,占总种数的86.08%;原产于美洲的种类最多,占总种数的70.24%;入侵等级为恶性入侵（1级）的物种有10科22种,严重入侵（2级）有13科22种,局部入侵（3级）、一般入侵（4级）和有待观察类（5级）分别有9、18和8种;恶性入侵和严重入侵的植物种类占入侵植物总数的55.70%。从分布格局和分布类型来看,以福州市的农田生态系统入侵植物种类最多,为52种;不同农田类型中,以旱地中的入侵植物种数最多,有74种;按分布区域划分的全域分布种共13种,按农田类型划分的全域分布种有11种。因此,福建省农田生态系统入侵植物种类繁多,分布广泛,原产地多元化,且恶性和严重入侵植物占比较高,入侵形势严峻,应加强入侵植物的动态监控与防范,以保护生物多样性和生态安全。     

中国外来入侵植物的等级划分与地理分布格局分析

基于文献报道、野外调查、标本记录和必要的分类学考证, 整理出我国外来入侵植物72科285属515种。根据外来入侵种的生物学与生态学特性、自然地理分布、入侵范围以及所产生的危害, 将其划分为5类: 即恶性入侵类(34种)、严重入侵类(69种)、局部入侵类(85种)、一般入侵类(80种)和有待观察类(247种)。通过地理分布格局分析, 中国外来入侵植物主要分布在我国西南及东部沿海地区, 并进一步扩散到内陆各省。中国外来入侵等级划分和地理分布格局可以作为外来入侵植物风险防范和管理的依据。本工作提供我国外来入侵植物的本底资料的同时, 还对主要外来入侵植物的管理提出了具体建议。     

Are boreal ecosystems susceptible to alien plant invasion? Evidence from protected areas

Although biological invasion by alien species is a major contributor to loss of indigenous biological diversity, few studies have examined the susceptibility of the boreal biome to invasion. Based on studies of other ecosystems, we hypothesized that alien plants will be restricted to disturbed areas near human activity and will not be found in natural areas of boreal ecosystems in Gros Morne National Park (Canada), a protected area experiencing a wide range of disturbance regimes. The distribution of alien plants in the region was evaluated using surveys, and study sites were established in naturally and anthropogenically disturbed habitats that had been invaded. Within study sites, randomization tests evaluated the importance of disturbance to alien plant invasion by examining changes in environmental conditions and species abundance within various disturbance regimes, while the importance of site characteristics limiting the distribution of alien plants were examined using Canonical Correspondence Analysis. Consistent with studies in a variety of biomes, areas of high disturbance and human activity had the greatest abundance of resources and the highest percentage of alien species. However, contrary to our hypothesis, natural areas of boreal ecosystems were found susceptible to alien plant invasion. Vegetation types vulnerable to invasion include forests, riparian areas, fens, and alpine meadows. Natural disturbance occurring in these vegetation types caused increases in bare ground and/or light availability facilitating alien plant invasion. Although high soil pH was associated with alien plants in these areas, disturbance was not found to cause changes in soil pH, suggesting susceptibility to invasion is pre-determined by bedrock geology or other factors influencing soil pH. Moose (Alces alces), a non-native herbivore, acts as the primary conduit for alien plant invasion in GMNP by dispersing propagules and creating or prolonging disturbance by trampling and browsing vegetation. The recurrent nature of disturbance within the boreal biome and its interaction with site conditions and herbivores enables alien plants to persist away from areas of high human activity. Managers of natural lands should monitor such interactions to decrease the invasion potential of alien plants.     

Differential processes underlying the roadside distributions of native and alien plant assemblages

Although biological invasion often alters ecosystem properties and community composition at different scales, considerable uncertainty still exists regarding the underlying mechanisms that regulate the spread of alien species into new habitats. An alien invasion is generally achieved through multiple processes from multiple sources; this type of invasion often prevents us from understanding of the dispersal mechanisms. Here, we aim to disentangle the processes of alien invasion by focusing on a single migration source. We surveyed the distribution of alien and native plant species in Shiretoko National Park, located in northern Japan. We measured the coverage of each species and the environmental and spatial factors in 362 quadrats established along roadsides. We found 101 native species and 35 alien species (γ-diversity) throughout the quadrats. The local species richness (α-diversity) was higher for the alien species (6.1 species) than for the native species (3.2 species). There was a significant negative correlation in α-diversity between native and alien species. Moreover, the α-diversity and distance from the nearest town (migration source) showed a negative relationship for alien assemblages while the native assemblages showed the opposite trend. These results suggest that the alien species are expanding their distribution outward from the town, resulting in a decrease in the α-diversity of native species in localities close to the migration source. Overall, our results emphasize that roadsides could unintentionally act as corridors for alien species, even in protected areas. Careful consideration is thus needed for utilizing these human-created habitats even though they were designed for conservation and management purposes.     

The global invasion success of Central European plants is related to distribution characteristics in their native range and species traits

Aim Determining which traits predispose a species to become invasive is a fundamental question of invasion ecology, but traits affect invasiveness in concert with other factors that need to be controlled for. Here, we explore the relative effects of biological traits of plant species and their distributional characteristics in the native range on invasion success at two stages of invasion. Location Czech Republic (for native species); and the world (for alien species). Methods The source pool of 1218 species of seed plants native to Central Europe was derived from the flora of the Czech Republic, and their occurrence in 706 alien floras all over the world was recorded, distinguishing whether they were listed as an ‘alien’ or a ‘weed’ in the latest version of Randall’s ‘Global compendium of weeds’ database. The latter type of occurrence was considered to indicate species ability to invade and cause economic impact, i.e. a more advanced stage of invasion. Using the statistical technique of regression trees, we tested whether 19 biological traits and five distributional characteristics of the species in their native range can be used to predict species success in two stages of invasion. Results The probability of a species becoming alien outside its native distribution range is determined by the size of its native range, and its tolerance of a wide range of climates acquired in the region of origin. Biological traits play only an indirect role at this stage of invasion via determining the size of the native range. However, the ability of species to become a weed is determined not only by the above characteristics of native distribution, but also directly by biological traits (life form and strategy, early flowering, tall stature, generative reproduction, number of ploidy levels and opportunistic dispersal by a number of vectors). Species phylogenetic relatedness plays only a minor role; it is more important at the lowest taxonomic levels and at the later stage of invasion. Main conclusion The global success of Central European species as ‘weeds’ is determined by their distributional characteristics in the native ranges and by biological traits, but the relative importance of these determinants depends on the stage of invasion. Species which have large native ranges and are common within these ranges should be paid increased attention upon introductions, and the above biological traits should be taken into account in screening systems applied to evaluate deliberate introductions of alien plants to new regions.     

遗传多样性与外来物种的成功入侵: 现状和展望

遗传多样性被认为是影响外来种入侵成功的重要因素之一。研究表明, 尽管外来种在入侵过程中可能受到奠基者效应的影响, 但是多次引种、种内或种间杂交等过程使得许多外来种在引入地的遗传多样性水平未必会显著低于原产地, 从而使得外来种可能通过快速进化来适应引入地的新生境。然而, 高水平的遗传多样性并非成功入侵的必要条件, 遗传变异的匮乏对一些外来种的入侵能力没有明显的影响, 甚至在一些生物入侵案例中, 遗传多样性的降低反而促进了入侵成功。针对遗传多样性与入侵成功之间的复杂关系, 本文在评述外来种遗传多样性的研究现状的基础上, 分析了遗传多样性对外来种的短期入侵成功和长期进化的影响机制, 从方法角度探讨了目前研究中存在的若干问题, 并对如何推进入侵生态学研究提出了一些看法。正如一些学者提出的, 入侵生态学需要与生态学其他分支整合起来, 才能加深对生物入侵及其相关的生态和进化过程的理解。     

A conceptual framework for understanding arthropod predator and parasitoid invasions

Arthropods make up the largest group of invasive alien species (IAS) worldwide. Although invasion research has been biased towards alien plants and vertebrates, it has suggested potential mechanisms for the success of IAS and provided a theoretical framework for further investigation. Here we address key concepts from invasion biology that are essential to our understanding of the success of invasive alien arthropod predators and parasitoids including human intervention, environmental characteristics, propagule pressure, biological traits, and biological interactions. To gain a greater understanding of the factors most likely to influence the different stages of invasion (arrival, establishment, and spread) for alien arthropod predators and parasitoids, we use a comparative approach to compare and contrast the differential success of invasions by alien phytophagous and carnivorous arthropods. Insights gained from this comparison suggest that future research will require a multitrophic approach in order to enhance our understanding of invasions at higher trophic levels.     

Relative importance of biological and human-associated factors for alien plant invasions in Hokkaido,Japan

Aims The invasion success of alien plants is strongly affected by both biological and human-associated factors. Evaluation of the relative contribution of each factor is important not only for the further understanding of invasion processes but also for the better management of invasion risk, particularly in protected areas of high conservation priority. Here, we quantified the relative importance of species biological traits and association with a human activity, i.e. agriculture, in explaining the invasion success of alien plants across the entire region and in protected areas in Hokkaido, Japan.     

Differences in evolutionary history translate into differences in invasion success of alien mammals in South Africa

Attempts to investigate the drivers of invasion success are generally limited to the biological and evolutionary traits distinguishing native from introduced species. Although alien species introduced to the same recipient environment differ in their invasion intensity – for example, some are “strong invaders”; others are “weak invaders” – the factors underlying the variation in invasion success within alien communities are little explored. In this study, we ask what drives the variation in invasion success of alien mammals in South Africa. First, we tested for taxonomic and phylogenetic signal in invasion intensity. Second, we reconstructed predictive models of the variation in invasion intensity among alien mammals using the generalized linear mixed‐effects models. We found that the family Bovidae and the order Artiodactyla contained more “strong invaders” than expected by chance, and that such taxonomic signal did not translate into phylogenetic selectivity. In addition, our study indicates that latitude, gestation length, social group size, and human population density are only marginal determinant of the variation in invasion success. However, we found that evolutionary distinctiveness – a parameter characterising the uniqueness of each alien species – is the most important predictive variable. Our results indicate that the invasive behavior of alien mammals may have been “fingerprinted” in their evolutionary past, and that evolutionary history might capture beyond ecological, biological and life‐history traits usually prioritized in predictive modeling of invasion success. These findings have applicability to the management of alien mammals in South Africa.