中国农业生态系统外来种入侵及其管理现状

农业生态系统极易遭受外来生物入侵。作者根据文献资料和多年工作观察统计出入侵我国农业生态系统的外来生物共计92科175属239种, 其中植物155种, 动物55种, 微生物29种, 植物多为有意引入后逸生, 而动物和微生物则主要是无意引入。外来入侵种发生数量呈现从南到北、从东到西逐渐减少的趋势。这些入侵种中, 来源于美洲的最多(占45.04%), 其次是欧洲(22.90%); 菜地(包括温室大棚)和果园入侵种最多, 分别达64.85%和66.53%, 而半年期的秋熟旱地和夏熟旱地分别占34.31%和23.85%。其中17种外来杂草、10种害虫、7种病原菌为恶性有害生物, 应作为防除的重点目标。目前农业生态系统外来入侵物种的控制以化学防治为主, 但由于长期施用化学农药, 在侵入我国农田的入侵种中, 已有51种在世界不同地区演化出抗药性生物型, 因而需重视生物防治、农业和生态防治以及检疫等的综合应用。今后外来种对农业生态系统的入侵格局、机制和趋势, 入侵途径以及生物入侵和抗药性生物型对农业生态系统中有害生物群落演替的影响、转基因作物导致的生物入侵等问题值得关注。     

农业活动对生物多样性的影响

农业生产活动如土地的农业利用、耕作、作物间套种植方式、放牧、农药化肥的使用以及农业动植物遗传改良（包括外来种引入）等是农业生产力提高的重要途径,同时也是影响生物多样性的重要因素之一。土地的不合理开发利用易导致生境破碎、生物多样性下降;大规模的机械耕作导致土壤动植物区系的变化,甚至某些物种的消失;农药（除草剂、杀虫剂等）的高度使用使非靶标动植物受到伤害;品种改良、外来种的引入以及远缘外源遗传物质的利用（如远缘杂交和ＤＮＡ导入分子育种）在丰富了遗传多样性的同时导致农作物类型和品种的简单化、一些古老的地方种和农家种等传统资源丢失等;而一些合理的农业措施（间套作、实行有机农场等）将有利于生物多样性的保持。农业活动注重的是农业生产力的提高而往往忽视其对农业系统中野生动植物（包括有害和无害）的影响以及野生动植物在维持系统稳定和平衡的作用。本文论述农业活动对生物多样性的影响以及生物多样性保护对提高农业生产力的作用,启示人们采取合理的农业活动方式,合理管理有害生物,减少农业活动对生物多样性的负面影响。     

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。     

主要外来鱼类对千岛湖生态系统的潜在影响及对策

生物入侵已在全球范围内广受关注,外来生物入侵现象日趋严重,不仅导致地区特有物种衰竭,还影响当地生物多样性、生态环境和经济发展。千岛湖(原名新安江水库)作为一个集渔业、水源、旅游、发电于一体的大型山谷型水库,其生态系统状况受到国内外生态学者的普遍关注。然而近年来,该水库也受到外来物种入侵威胁,对土著鱼类尤其是经济鱼类的资源构成了巨大的威胁。综合分析了千岛湖生态系统的主要特征和主要外来鱼种,结合这些外来鱼类的生物学特征,概述主要外来鱼类对千岛湖生态系统的潜在影响,并针对这些潜在风险,提出了相应的治理对策,为千岛湖水域生态系统的管理工作积累基础资料。     

青城山森林公园兽类和鸟类资源初步调查: 基于红外相机数据

<正>陆生脊椎动物是生物多样性保护和管理评价的重要指示类群(Morrison et al.,2007;Liu et al.,2013)。全球多数生态系统中,许多大中型脊椎动物的种群数量在急剧下降,不少物种甚至遭遇灭顶之灾。而人类活动影响(如猎杀、森林砍伐、外来物种侵入、栖息地破坏和片断化等)是引起这些野生动物种群和群落变化的直接或间接原因(Morrison et al.,2007)。同时,野生动物种群和群落变化对生态系统其他物种也产生了严重的生态后果,如食果动物的     

水盾草—南四湖外来水生植物新记录及其生境特点

外来生物入侵与生境改变被认为是导致全球生物多样性下降的两大主因[1]。其中入侵植物通过营养竞争、植被结构改变、化感作用等,影响土著植物种群和群落,进而影响生态系统结构和功能。水生植物的入侵已成为影响我国淡水水体景观和生物多样性的重要因素[2—4]。水盾草     

景观生态学原理在保护生物学中的应用

人类活动所引起的自然生境片断化被认为是全球范围内生物多样性急剧下降的最主要原因"－'。保护生物多样性已成为全世界关注的重大问题。近年来迅速发展的保护生物学是一门既面向目前生物危机,又着眼于长远生态前景的,以研究物种、群落和生态系统的动态和问题为对象的新兴学     

加拿大一枝黄花--一种正在迅速扩张的外来入侵植物

加拿大一枝黄花Solidago canadensis原产于北美,现已入侵到欧洲、亚洲和大洋洲等地,成为一种世界性的入侵性外来杂草,威胁着生态系统的生物多样性和农业生产,并造成显著的环境与经济损失。1935年,该物种作为庭院植物被引入上海,后逸生成为杂草,目前正在我国境内尤其是东部地区迅速扩散。本文较系统地介绍了加拿大一枝黄花在形态学、生物系统学、遗传多样性和生活史等方面的特征,并试图从其入侵力（繁殖力、化感作用、菌根营养）、被入侵生态系统的可入侵性（适宜的气候、生境破坏、天敌释放和土壤氮水平的影响）以及人类活动的直接影响等三方面分析其入侵成功的原因。最后,提出加拿大一枝黄花的防治关键在于控制其有性繁殖,现有的人工铲除和化学防治等措施都应在其有性繁殖之前实施。     

威胁因素之外来植物

外来生物入侵在当今世界范围内广泛发生,而且,它们对地球的影响已经构成全球变化的重要成分,其对生物多样性、生态系统功能、生物进化以及景观影响深远,给环境和人类经济造成无法挽回的损失,已成为世界性灾难。20世纪80年代以来,入侵植物对我国农林牧业等领域造成的危害日趋严重,也对经济和社会发展造成多重负面影响。     

生物入侵对黄河流域生态系统的影响及对策

黄河流域健康的生态系统是沿黄地区生态保护和高质量发展的核心。然而, 随着经济高速发展和人类活动增加, 大量的外来生物传入并占据黄河流域生态位。这些外来生物在黄河流域的大肆扩繁给黄河流域本土生物和生态系统带来了严重威胁, 甚至严重影响人类健康。因此, 研究黄河流域的外来生物入侵问题, 并提出保护对策, 对于黄河流域生态保护和高质量发展具有重大意义。本文主要从黄河流经九省区(包含黄河流域)外来入侵生物的传入特征、传播途径、种群动态、成灾机制以及入侵生物对黄河流域重要生物资源和生态系统的影响等方面进行综述, 并提出了防控黄河流域生物入侵、保护黄河流域健康的生态系统的措施和对策。     

Global change and species interactions in terrestrial ecosystems

The main drivers of global environmental change (CO₂ enrichment, nitrogen deposition, climate, biotic invasions and land use) cause extinctions and alter species distributions, and recent evidence shows that they exert pervasive impacts on various antagonistic and mutualistic interactions among species. In this review, we synthesize data from 688 published studies to show that these drivers often alter competitive interactions among plants and animals, exert multitrophic effects on the decomposer food web, increase intensity of pathogen infection, weaken mutualisms involving plants, and enhance herbivory while having variable effects on predation. A recurrent finding is that there is substantial variability among studies in both the magnitude and direction of effects of any given GEC driver on any given type of biotic interaction. Further, we show that higher order effects among multiple drivers acting simultaneously create challenges in predicting future responses to global environmental change, and that extrapolating these complex impacts across entire networks of species interactions yields unanticipated effects on ecosystems. Finally, we conclude that in order to reliably predict the effects of GEC on community and ecosystem processes, the greatest single challenge will be to determine how biotic and abiotic context alters the direction and magnitude of GEC effects on biotic interactions.     

How does climate change cause extinction?

Anthropogenic climate change is predicted to be a major cause of species extinctions in the next 100 years. But what will actually cause these extinctions? For example, will it be limited physiological tolerance to high temperatures, changing biotic interactions or other factors? Here, we systematically review the proximate causes of climate-change related extinctions and their empirical support. We find 136 case studies of climatic impacts that are potentially relevant to this topic. However, only seven identified proximate causes of demonstrated local extinctions due to anthropogenic climate change. Among these seven studies, the proximate causes vary widely. Surprisingly, none show a straightforward relationship between local extinction and limited tolerances to high temperature. Instead, many studies implicate species interactions as an important proximate cause, especially decreases in food availability. We find very similar patterns in studies showing decreases in abundance associated with climate change, and in those studies showing impacts of climatic oscillations. Collectively, these results highlight our disturbingly limited knowledge of this crucial issue but also support the idea that changing species interactions are an important cause of documented population declines and extinctions related to climate change. Finally, we briefly outline general research strategies for identifying these proximate causes in future studies.     

The biogeography of avian extinctions on oceanic islands

Aim To test the influences of island area, island isolation, and human‐introduced mammalian predators on avian extinctions that have occurred on oceanic islands worldwide. Location The oceanic islands of the world. Methods We augmented and re‐examined an existing data set for 218 oceanic islands by means of causal modelling using path analysis (a form of structural equation modelling) and a null model. Results The number of extinctions was not a simple function of the number of bird species on the various islands. Whereas introduced mammalian predators had an influence on the number of extinctions, island area (via indirect influences) and isolation (via direct influences) were equally or more important. Main conclusions The multiple influences of physical and biotic factors on past extinctions can be revealed through modelling the causal influences of physical attributes of islands on biological characteristics, and the causal influences of both physical and biological characteristics on extinctions.     

On defining and quantifying biotic homogenization

Ongoing species invasions and extinctions are changing biological diversity in different ways at different spatial scales. Biotic homogenization (or BH) refers to the process by which the genetic, taxonomic or functional similarities of regional biotas increase over time. It is a multifaceted process that encompasses species invasions, extinctions and environmental alterations, focusing on how the identities of species (or their genetic or functional attributes) change over space and time. Despite the increasing use of the term BH in conservation biology, it is often used erroneously as a synonym for patterns of species invasions, loss of native species or changes in species richness through time. This reflects the absence of an agreed-upon, cogent definition of BH. Here, we offer an operational definition for BH and review the various methodologies used to study this process. We identify the strengths and weaknesses of these approaches, and make explicit recommendations for future studies. We conclude by citing the need for researchers to: (1) consider carefully the definition of BH by recognizing the genetic, taxonomic and functional realms of this process; (2) recognize that documenting taxonomic homogenization requires tracking the identity of species (not species richness) comprising biotas through space and time; and (3) employ more rigorous methods for quantifying BH.     

Multigene CRISPR/Cas9 genome editing of hybrid proline rich proteins (HyPRPs) for sustainable multi-stress tolerance in crops: the review of a promising approach

Physiology and Molecular Biology of Plants - The recent global climate change has directly impacted major biotic and abiotic stress factors affecting crop productivity worldwide. Therefore, the...     

Why are some weta (Orthoptera: Stenopelmatidae) vulnerable yet others are common?

The large (4 g) to very large (40 g) stenopelmatid orthopterans of New Zealand are known collectively as weta. A consideration of 20 species of Hemideina, Deinacrida and tusked weta reveals that at one end of a vulnerability gradient are those species which thrive in the presence of key predators (rats), while at the other end are species that have become extinct on the mainland but still survive on predator-free island refuges. Habitat modification does not appear to be a factor in these extinctions. This paper reviews the lifestyles and some important biotic parameters that seem to determine their relative vulnerability along this gradient. When predators are present, the factors leading to extinction are large body size, use of temporary refuges, protective quality of the refuges, time spent on the ground and the effectiveness of their defensive behaviour.     

Lessons from a kill

During their colonization by Polynesians and later by Europeans, the Hawaiian islands suffered a massive loss of species. All the extinctions are indirectly attributable to human impact. Nonetheless, it has proved extremely difficult to specify which of several possible mechanisms caused each particular extinction. This seems to admit defeat in the battle to understand past extinctions. Such understanding could guide our efforts to protect species that are now threatened with extinction. Will it be easier to understand the causes of future extinctions? Surveys of future extinctions stress habitat destruction as the simple and dominant mechanism. This contrasts to its secondary (and generally confused) role in past extinctions. I argue that this contrast between the complexity of the past and the apparent simplicity of the future arises because extinction mechanisms are inherently synergistic. Once extensive species losses begin, it may be impossible to separate the mechanisms and thus manage an individual species as if its decline had a single cause.     

Patterns of Fusarium community structure and abundance in relation to spatial, abiotic and biotic factors in soil

Members of the Fusarium genus are important components of many plant–soil systems worldwide and are responsible for many crop diseases. Knowledge of the relative influence of biotic and abiotic factors on this genus is therefore of broad economic and ecological importance. In order to address this issue, we examined Fusarium communities in soils nearby apparently healthy and symptomatic asparagus plants in 50 fields scattered in four agricultural regions of Québec, Canada. Fusarium community structure and abundance were assessed using genus-specific PCR-denaturing gradient gel electrophoresis and CFU counts, respectively. Multivariate statistical analyses were used to detect community patterns related to spatial, abiotic and biotic factors. Results suggested that Fusarium community structure (i.e. the presence and absence of the different Fusarium sequence variants in the samples) in soil is mainly related to biotic factors (arbuscular mycorrhizal fungi and bacterial community structure), whereas Fusarium abundance is more closely related to abiotic factors (mainly clay, organic matter, NH₄, Na and Cu). Some degree of influence of spatial patterns was also observed on both Fusarium community structure and abundance with, for instance, a large regional variation in Fusarium community structure. However, Fusarium community structure was not directly related to the disease status of nearby asparagus plants.     

Role of Osmotin in Strawberry Improvement

In nature, plants are often exposed to multiple biotic and abiotic stresses, severely affecting their growth and development and reducing their productivity. Future predicted adverse climatic changes might threaten the very sustainability of crop production worldwide. Various approaches ought to be explored to deal with the challenges of sustained crop production under such conditions. In this review, we explore the potential of osmotin, a stress-responsive multifunctional pathogenesis-related (PR)-5c protein from tobacco, in improving adaptability of crop plants to climatic changes. As osmotin plays an important role in salt and drought tolerance as well as in cold tolerance and in protecting plants against some fungal pathogens, the relevance of osmotin in improving tolerance to abiotic and biotic stresses in strawberry, a salt-sensitive plant that is also susceptible to several fungal pathogens, is presented herein.     

Differential effects of abiotic conditions on fitness-related parameters of two <Emphasis Type="Italic">Euseius</Emphasis> species inhabiting avocado agro-ecosystems

Temperature and relative humidity are important factors in shaping the structure and dynamics of communities composed of ectothermic species, as they directly affect fitness-related parameters and biotic interactions. In a climate change context, increased warming and dryness will likely affect arthropod communities of agro-ecosystems managed by biological pest control. In this work, we compare, at the individual level, the functional relation between temperature and relative humidity and different life-history parameters in two sister predatory mite species that inhabit Spanish avocado crops, Euseius stipulatus and E. scutalis (Athias-Henriot) (Acari: Phytoseiidae). We found that negative effects of high temperature and low relative humidity were stronger in E. stipulatus than in E. scutalis. That E. scutalis tolerates very well hot and dry environments makes the species a good candidate to be considered in the future as a biocontrol agent against pests in subtropical and Mediterranean orchards.