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维基百科

入侵物种

入侵物种引进物种的一个子集。如果一个物种經人为引入一个其先前不曾自然生存的地区,并有能力在无更多人为干预的情况下在当地发展成一定数量,以至威胁到当地的生物多樣性,成为当地公害,就可称之为「入侵物种」。

入侵美國東南部的日本藤物,廣泛生長於喬治亞州亞特蘭大市,被視為入侵物種。

簡介

虽然入侵物种经常定义为成为祸害的引進种,但有些物种天生就能在特定的区域,在人类活动的影响下繁殖并成为当地的一个入侵种。澳大利亚东南部的杂色澳洲喜鹊(Pied Currawong)就是一个例子:由于人类对当地景观的改变,使得杂色澳洲喜鹊的数量在20世纪急剧增长。杂色澳洲喜鹊捕食其他小型鸟类的雏鸟,使得该地区其他小型鸟类数量锐减。在夏威夷,一种称「'ae'ae」的湿地植物(当地的假馬齒莧)也被視為有害物种,因其快速增长覆盖了原本作為保护黑翅長腳鷸Himantopus mexicanus knudseni)之用的浅水塘,使得这些区域不再适合这种濒危鸟类觅食。当然,地球上所有的物种都有数量增减周期,一般来说均在一定范围内进行波动。这类变化一般是由环境上的各种因素变化导致,而其中以由人类活动所带来的地貌改变的影响显得最为突出。

入侵条件

所有物种都是竞争中求生存的,但入侵物种有着其独特的特点使其超越本土物种。有时,这种优势体现在生长速度和繁殖速率上,有时,物种间更加直接的相互作用。

然而研究者不认为这个有着标定入侵物种的代表性。86%的入侵物种可以由这些特征来鉴别。另一项研究发现,入侵物种只占了有这些特征的物种中的很小的一部分,有这些特点的物种最终被认定为非入侵物种,从而需要其他的一些解释。

通常,入侵物种的共同特点有:

  • 高生长速度
  • 强大繁殖能力
  • 快速蔓延的能力
  • 表现性弹性(可以改变生长模式以适应现有环境)
  • 可耐受各种环境
  • 一个很广的生態幅度
  • 与人类有关

通常外来物种需要存活过种群低密度的时期,才有可能在新的地点变成入侵物种。种群数量很少的时候,外来物种很难繁殖并存活下来,所以一个物种也许需要很多次到达一个地点才可能在这里存活。而人类的周期性的往返活动,如船只在港口间的运输和汽车上下高速路,给了这些物种更多的机会。

当外来物种可以在争夺养料、阳光、空间、水或食物中战胜土著种,它便可能变成入侵物种。如果这些物种是在强烈的竞争或是巨大捕食压力中进化的,而新的环境中没有竞争者,这些入侵者就可以很快的增长。对于一个所有资源都予以充分利用的生态系统,入侵物种每一点获利都是土著种的损失。然而,这种单方的竞争优越性导致的土著种最终灭绝并不是一蹴而就的,它们可以共存相当的一段时间,渐渐地当入侵物种的种群数量明显提升,慢慢适应了环境之后,竞争优势也变得明显了。

入侵物种往往可以利用那些土著种无法利用的资源,比如依靠强健根系可以利用的深层水资源,可以在之前没有物种的土壤类型中生存。刺山羊草(Aegilops triuncialis)被引进到加州的水保持度低,缺乏营养物质,高镁钙,且有重金属毒性的土壤中。这种土壤中一般植物密度都很低,但是山羊草可以在这里繁茂生长,排挤了这些土地中的土著种。

当物种使用化学或生物方式抑制竞争者生存时,这个过程就加速进行了。一种机制就是拮抗作用,即一种植物释放化学物质使得周围的土壤对于竞争物种无法生存。

改变生境的火灾状况是另一种促进方式。旱雀麦原产欧亚大陆,它不仅可以在火灾之后快速繁殖扩散,还可以通过产生大量的干燥碎屑增加火灾频率和强度,尤其在北美的火灾常发的季节。在旱雀麦广泛分布的地区,它显著的改变了当地的火灾频率以至于其他物种无法在这种高频火灾中存活下来,使得旱雀麦保持统治性并且不断扩展。

对于环境的物理形貌改变也是促进的模式之一。

历史观点

案例

台灣福壽螺是最有名的入侵物種之一。原本從南美洲引進做為食用螺類,但因口感不佳而被棄養於水溝,但反而開始大量繁殖,對於農作物造成危害。例如紅火蟻小花蔓澤蘭褐根病菌(樹木褐根病病原菌)、布袋蓮、家貓、家犬亦造成危害。

另外罗非鱼是從新加坡引進的,雖然是常見的食用魚類,但是放養於水庫湖泊的罗非鱼由於攻擊性強,逐漸排擠其他水生動物的生存空間。中華絨毛蟹大閘蟹)在台灣中北部的一些山區水域亦有其蹤跡,被研判是從附近養殖池中逃脫後開始繁衍的。 而近年被發現的「十足目虹彩病毒」也是一種入侵物種,是由走私的蝦蟹所傳播的。

在南半球松属植物也是常见的入侵物种。大部分松属植物原生于北半球,作为景观植物被引入南半球后,因为其种子的特殊结构可以通过风媒传播,同时因为其优秀的耐寒性使其更容易在高海拔和高纬度地区形成聚落。[1]

生物学控制

 
亞洲虎蚊Aedes albopictus)正在叮咬人類。

生物学控制就是一种生物控制另一种生物,即引进当前入侵生物的天敌,使用天敌进行数量的控制,但该种方法的主要问题来自于引进的生物可能成为新的入侵生物,对当地的生态环境进一步地破坏。

生物地理學評價

生物地理學評價將入侵物種分為五類。

階段 特性
0 正常
I 外來
II 引入
III 在該地區上數位及集中度屬於罕見
IVa 普遍但罕見
IVb 集中但未支配
V 集中和出現支配

其他条目

外部链接

  • Invasive Species Specialist Group(页面存档备份,存于互联网档案馆
  • CEQ (1999). Web site page with text.
  • U.S. Government (National Agricultural Library) website on invasive species (页面存档备份,存于互联网档案馆).
  • "The Ecology of Invasions by Animals and Plants" (页面存档备份,存于互联网档案馆
  • Natives Vs. Exotics, The Myth of the Menace, by David I. Theodoropoulos (页面存档备份,存于互联网档案馆
  • 全球入侵種資料庫(GISD) (页面存档备份,存于互联网档案馆

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  1. ^ Higgins, Steven I.; Richardson, David M.; Steven I. Higgins David & M. Richardson. Pine invasions in the southern hemisphere: modelling interactions between organism, environment and disturbance.. Plant Ecology. 1998, 135 (1): 79–93. doi:10.1023/A:1009760512895. 

入侵物种, 此条目的主題是有害的引進物種, 关于無害的引進物種, 請見, 外來種, 是引进物种的一个子集, 如果一个物种經人为引入一个其先前不曾自然生存的地区, 并有能力在无更多人为干预的情况下在当地发展成一定数量, 以至威胁到当地的生物多樣性, 成为当地公害, 就可称之为, 入侵美國東南部的日本藤物葛, 廣泛生長於喬治亞州亞特蘭大市, 被視為入侵物種, 目录, 簡介, 入侵条件, 历史观点, 案例, 生物学控制, 生物地理學評價, 其他条目, 外部链接, 參考資料簡介, 编辑虽然经常定义为成为祸害的引進种, 但有. 此条目的主題是有害的引進物種 关于無害的引進物種 請見 外來種 入侵物种是引进物种的一个子集 如果一个物种經人为引入一个其先前不曾自然生存的地区 并有能力在无更多人为干预的情况下在当地发展成一定数量 以至威胁到当地的生物多樣性 成为当地公害 就可称之为 入侵物种 入侵美國東南部的日本藤物葛 廣泛生長於喬治亞州亞特蘭大市 被視為入侵物種 目录 1 簡介 2 入侵条件 3 历史观点 3 1 案例 3 2 生物学控制 4 生物地理學評價 5 其他条目 6 外部链接 7 參考資料簡介 编辑虽然入侵物种经常定义为成为祸害的引進种 但有些物种天生就能在特定的区域 在人类活动的影响下繁殖并成为当地的一个入侵种 澳大利亚东南部的杂色澳洲喜鹊 Pied Currawong 就是一个例子 由于人类对当地景观的改变 使得杂色澳洲喜鹊的数量在20世纪急剧增长 杂色澳洲喜鹊捕食其他小型鸟类的雏鸟 使得该地区其他小型鸟类数量锐减 在夏威夷 一种称 ae ae 的湿地植物 当地的假馬齒莧 也被視為有害物种 因其快速增长覆盖了原本作為保护黑翅長腳鷸 Himantopus mexicanus knudseni 之用的浅水塘 使得这些区域不再适合这种濒危鸟类觅食 当然 地球上所有的物种都有数量增减周期 一般来说均在一定范围内进行波动 这类变化一般是由环境上的各种因素变化导致 而其中以由人类活动所带来的地貌改变的影响显得最为突出 入侵条件 编辑所有物种都是竞争中求生存的 但入侵物种有着其独特的特点使其超越本土物种 有时 这种优势体现在生长速度和繁殖速率上 有时 物种间更加直接的相互作用 然而研究者不认为这个有着标定入侵物种的代表性 86 的入侵物种可以由这些特征来鉴别 另一项研究发现 入侵物种只占了有这些特征的物种中的很小的一部分 有这些特点的物种最终被认定为非入侵物种 从而需要其他的一些解释 通常 入侵物种的共同特点有 高生长速度 强大繁殖能力 快速蔓延的能力 表现性弹性 可以改变生长模式以适应现有环境 可耐受各种环境 一个很广的生態幅度 与人类有关通常外来物种需要存活过种群低密度的时期 才有可能在新的地点变成入侵物种 种群数量很少的时候 外来物种很难繁殖并存活下来 所以一个物种也许需要很多次到达一个地点才可能在这里存活 而人类的周期性的往返活动 如船只在港口间的运输和汽车上下高速路 给了这些物种更多的机会 当外来物种可以在争夺养料 阳光 空间 水或食物中战胜土著种 它便可能变成入侵物种 如果这些物种是在强烈的竞争或是巨大捕食压力中进化的 而新的环境中没有竞争者 这些入侵者就可以很快的增长 对于一个所有资源都予以充分利用的生态系统 入侵物种每一点获利都是土著种的损失 然而 这种单方的竞争优越性导致的土著种最终灭绝并不是一蹴而就的 它们可以共存相当的一段时间 渐渐地当入侵物种的种群数量明显提升 慢慢适应了环境之后 竞争优势也变得明显了 入侵物种往往可以利用那些土著种无法利用的资源 比如依靠强健根系可以利用的深层水资源 可以在之前没有物种的土壤类型中生存 刺山羊草 Aegilops triuncialis 被引进到加州的水保持度低 缺乏营养物质 高镁钙 且有重金属毒性的土壤中 这种土壤中一般植物密度都很低 但是山羊草可以在这里繁茂生长 排挤了这些土地中的土著种 当物种使用化学或生物方式抑制竞争者生存时 这个过程就加速进行了 一种机制就是拮抗作用 即一种植物释放化学物质使得周围的土壤对于竞争物种无法生存 改变生境的火灾状况是另一种促进方式 旱雀麦原产欧亚大陆 它不仅可以在火灾之后快速繁殖扩散 还可以通过产生大量的干燥碎屑增加火灾频率和强度 尤其在北美的火灾常发的季节 在旱雀麦广泛分布的地区 它显著的改变了当地的火灾频率以至于其他物种无法在这种高频火灾中存活下来 使得旱雀麦保持统治性并且不断扩展 对于环境的物理形貌改变也是促进的模式之一 历史观点 编辑案例 编辑 在台灣 福壽螺是最有名的入侵物種之一 原本從南美洲引進做為食用螺類 但因口感不佳而被棄養於水溝 但反而開始大量繁殖 對於農作物造成危害 例如紅火蟻 小花蔓澤蘭 褐根病菌 樹木褐根病病原菌 布袋蓮 家貓 家犬亦造成危害 另外罗非鱼是從新加坡引進的 雖然是常見的食用魚類 但是放養於水庫 湖泊的罗非鱼由於攻擊性強 逐漸排擠其他水生動物的生存空間 中華絨毛蟹 大閘蟹 在台灣中北部的一些山區水域亦有其蹤跡 被研判是從附近養殖池中逃脫後開始繁衍的 而近年被發現的 十足目虹彩病毒 也是一種入侵物種 是由走私的蝦蟹所傳播的 在南半球松属植物也是常见的入侵物种 大部分松属植物原生于北半球 作为景观植物被引入南半球后 因为其种子的特殊结构可以通过风媒传播 同时因为其优秀的耐寒性使其更容易在高海拔和高纬度地区形成聚落 1 生物学控制 编辑 亞洲虎蚊 Aedes albopictus 正在叮咬人類 生物学控制就是一种生物控制另一种生物 即引进当前入侵生物的天敌 使用天敌进行数量的控制 但该种方法的主要问题来自于引进的生物可能成为新的入侵生物 对当地的生态环境进一步地破坏 生物地理學評價 编辑生物地理學評價將入侵物種分為五類 階段 特性0 正常I 外來II 引入III 在該地區上數位及集中度屬於罕見IVa 普遍但罕見IVb 集中但未支配V 集中和出現支配其他条目 编辑入侵植物 入侵物种列表 世界百大外来入侵种外部链接 编辑Invasive Species Specialist Group 页面存档备份 存于互联网档案馆 CEQ 1999 Web site page with Executive Order 13112 text U S Government National Agricultural Library website on invasive species 页面存档备份 存于互联网档案馆 The Ecology of Invasions by Animals and Plants 页面存档备份 存于互联网档案馆 Natives Vs Exotics The Myth of the Menace by David I Theodoropoulos 页面存档备份 存于互联网档案馆 全球入侵種資料庫 GISD 页面存档备份 存于互联网档案馆 參考資料 编辑Ayres D et al 2004 Spread of exotic cordgrasses and hybrids Spartina sp in the tidal marshes of San 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diseases West Nile virus Available at CDC 页面存档备份 存于互联网档案馆 Dec 1 2005 Cornell University 2005 Biological Control a guide to natural enemies in North America World Wide Web page Available www nysaes cornell edu ent biocontrol Dec 1 2005 Council on Environmental Quality 1999 Executive order 13112 World Wide Web page Available https web archive org web 20080515154626 http ceq eh doe gov nepa regs eos eo13112 html Dec 1 2005 Davis MA Grime JP Thompson K 2000 Fluctuating resources in plant communities a general theory of invisibility Journal of Ecology 88 3 528 534 Dukes JS 2001 Biodiversity and invisibility in grassland microcosms Oecologia 126 4 563 568 Eiswerth M E 2005 Input output modeling outdoor recreation and the economic impacts of weeds Weed Science 53 130 137 Elton C S 1958 The Ecology of Invasions by Animals and Plants University of Chicago Press Chicago Reprinted 2000 with a foreword by Daniel Simberloff 196pp ISBN 0 226 20638 6 Ewell J J D J O Dowd J Bergelson C C Daehler C M D 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Rejmanek M and Richardson D M 1996 What attributes make some plant species more invasive Ecology 77 18 14 13 August 2006 Rhymer J M and Simberloff D 1996 Extinction by hybridization and introgression Annual Review of Ecology and Systematics 27 83 109 Sakai A K F W Allendorf J S Holt D M Lodge J Molofsky K A With S Baughman R J Cabin J E Cohen N C Ellstrand D E McCauley P O Neil I M Parker J N Thompson and S G Weller 2001 The Population Biology of Invasive Species Annual Review of Ecology and Systematics 32 1 305 332 Sax D F S D Gaines and J H Brown 2002 Species Invasions Exceed Extinctions on Islands Worldwide A Comparative Study of Plants and Birds American Naturalist 160 766 783 Silver Botts P B A Patterson and D Schlosser 1996 Zebra mussel effects on benthic invertebrates physical or biotic Journal of the North American Benthological Society 15 179 184 Simberloff D 2001 Biological invasions How are they affecting us and what can we do about them Western North American Naturalist 61 308 315 Simberloff Daniel 2004 Book Review Invasion Biology Critique of a Psedoscience Ecological Economics 48 360 362 Smith J P Jr and K Berg 1988 Inventory of rare and endangered vascular plants of California California Native Plant Society Sacramento California Stachowicz J J and D Tilman 2005 Species invasions and the relationships between species diversity community saturation and ecosystem functioning In D F Sax J J Stachowicz and S D Gaines eds Species Invasions Insights into Ecology Evolution and Biogeography Sinauer Associates Sunderland Massachusetts USA Stadler B T Muller D Orwig and R Cobb 2005 Hemlock woolly adelgid in New England forests Canopy impacts transforming ecosystem processes and landscapes Ecosystems 8 233 247 Stohlgren T J D T Barnett and J T Kartesz 2003 The rich get richer patterns of plant invasions in the United States Frontiers in Ecology and the Environment 1 11 14 Stohlgren T J D Binkley G W Chong M A Kalkhan L D Schell K A Bull Y Otsuki G Newman M Bashkin and Y Son 1999 Exotic plant species invade hot spots of native plant diversity Ecological Monographs 69 25 46 The Nature Conservancy 2005 The Global Species Initiative World Wide Web page Available https web archive org web 20070713214553 http tncweeds ucdavis edu esadocs html Dec 1 2005 Thebaud C Finzi AC Affre L Debussche M Escarre J 1996 Assessing why two introduced Conyza differ in their ability to invade Mediterranean old fields Ecology 77 3 791 804 Theodoropoulos David 2003 Invasion Biology Critique of a Pseudoscience Avvar Books Blythe CA 237 p ISBN 0 9708504 1 7 Tilman D 2004 Niche tradeoffs neutrality and community structure A stochastic theory of resource competition invasion and community assembly Proceedings of the National Academy of Sciences 101 10854 10861 Townsend CR 1991 Exotic Species Management and the Need for a Theory of Invasion Ecology New Zealand Journal of Ecology 15 1 1 3 Van Driesche J Van Driesche R 2000 Nature out of place biological invasions in the global age Washington D C Island Press Verling E G M Ruiz L D Smith B Galil A W Miller and K R Murphy 2005 Supply side invasion ecology characterizing propagule pressure in coastal ecosystems Proceedings of the Royal Society of London Ser B Biological Science 272 1249 1256 Vivanco JM Bais HP Stermitz FR Thelen GC Callaway RM 2004 Biogeographical variation in community response to root allelochemistry novel weapons and exotic invasion Ecology Letters 7 4 285 292 Williams J D and G K Meffe 1998 Nonindigenous Species In Status and Trends of the Nation s Biological Resources Volume 1 Reston Virginia United States Department of the Interior Geological Survey Gurevitch J Scheiner S Fox G 2002 The Ecology of Plants Chapter 14 pp 281 282 Higgins Steven I Richardson David M Steven I Higgins David amp M Richardson Pine invasions in the southern hemisphere modelling interactions between organism environment and disturbance Plant Ecology 1998 135 1 79 93 doi 10 1023 A 1009760512895 引文使用过时参数coauthors 帮助 取自 https zh wikipedia org w index php title 入侵物种 amp oldid 76863414, 维基百科,wiki,书籍,书籍,图书馆,

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