爱沙尼亚沿海海域的甲壳类动物入侵

K. Herkül, J. Kotta, T. Püss, L. Kotta
{"title":"爱沙尼亚沿海海域的甲壳类动物入侵","authors":"K. Herkül, J. Kotta, T. Püss, L. Kotta","doi":"10.3176/ECO.2009.4.06","DOIUrl":null,"url":null,"abstract":"INTRODUCTION Together with habitat loss and climate change, invasions of nonindigenous species are one of the most serious threats to global biodiversity. This human-aided process has initiated significant, unpredictable, and irreversible changes to both the abiotic and the biotic environment and has caused severe economic damage in a variety of waterbodies worldwide (e.g. Canton, 1996; Vitousek et al., 1997; Sala et al., 2000). Concurrently with this global trend several new crustacean species have also been found in the Estonian coastal sea in recent years. The gammarid amphipod Gammarus tigrinus Sexton originates from the North American coast of the Atlantic Ocean. The species was introduced to Europe probably in ballast water and was first discovered in England in 1931 (Chambers, 1977). Although G. tigrinus was found in the Baltic Sea already in 1975, its significant range expansion started in the 1990s (Jazdzewski et al., 2002, 2005; Szaniawska et al., 2003). In the northern Baltic Sea G. tigrinus was first found in the northern Gulf of Riga (Herkul et al., 2006) and the northern Gulf of Finland in 2003 (Pienimaki et al., 2004). In 2005, G. tigrinus was found in the Neva Estuary, the easternmost part of the Gulf of Finland (Berezina, 2007). This species has caused a significant decrease in the diversity and density of native amphipods in the southern Baltic Sea (Grabowski et al., 2006) and Estonian coastal sea (Kotta et al., 2006; Orav-Kotta et al., 2009). The amphipod Chelicorophium curvispinum (Sars) originates from large rivers connected to the Black Sea and the Caspian Sea. It was found in the Baltic Sea already in the 1920s (Bij de Vaate et al., 2002). The species invaded to the Baltic and North seas through rivers and canals attached to the hulls of ships and in ballast water. Regardless of its long invasion history in the Baltic Sea, C. curvispinum was not found in the northern Baltic until 2005 when it was detected in the eastern part of the Estonian coast of the Gulf of Finland (Herkul & Kotta, 2007). In the next year, 2006, C. curvispinum was found in Luga Bay, Russia (Malyavin et al., 2008). Similarly to C. curvispinum, the gammarid amphipod Pontogammarus robustoides (Sars) originates from the lower reaches of Ponto-Caspian rivers and from brackish and freshwater lakes around the Black Sea (Bij de Vaate et al., 2002). In 1960-1961, the species was intentionally introduced into the Kaunas Water Reservoir on the Nemunas River, Lithuania (Bij de Vaate et al., 2002; Gumuliauskaite & Arbaciauskas, 2008). It successfully spread in the Nemunas drainage system including the Curonian Lagoon of the Baltic Sea. In 1999 P. robustoides was first found in Neva Bay, the easternmost part of the Gulf of Finland (Panov et al., 2003) and in 2006, in Lake Ladoga (Kurashov & Barbashova, 2008). In 2006 the species was recorded for the first time in the Estonian coastal sea. Similarly to G. tigrinus, P. robustoides has a potential to reduce the diversity and density of native gammarids (Panov et al., 2003; Gumuliauskaite & Arbaciauskas, 2008). The mysids Paramysis intermedia (Czerniavsky) and P. lacustris (Czerniavsky) are native to rivers connected to the Caspian Sea and Black Sea (Birshteina et al., 1968). In the 1970s P. lacustris and P. intermedia were introduced to Lake Peipsi but neither of the species has been sighted later (Timm et al., 2001). Both species were also introduced to Lake Vortsjarv, southern Estonia, in the 1970s, but only P. lacustris formed a permanent population there (Kangur et al., 2004). However, there is only a single record of P. lacustris in the Estonian coastal sea dating back to 1963 (Yarvekyulg, 1979). We are not aware of any successful introductions of P. intermedia in the Baltic Sea drainage area while P. lacustris inhabits the Curonian Lagoon, the southern Baltic Sea, already since the 1960s. In 2008 P. intermedia was found for the first time in the Baltic Sea. …","PeriodicalId":262667,"journal":{"name":"Estonian Journal of Ecology","volume":"1 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2009-12-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"31","resultStr":"{\"title\":\"Crustacean invasions in the Estonian coastal sea\",\"authors\":\"K. Herkül, J. Kotta, T. Püss, L. Kotta\",\"doi\":\"10.3176/ECO.2009.4.06\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"INTRODUCTION Together with habitat loss and climate change, invasions of nonindigenous species are one of the most serious threats to global biodiversity. This human-aided process has initiated significant, unpredictable, and irreversible changes to both the abiotic and the biotic environment and has caused severe economic damage in a variety of waterbodies worldwide (e.g. Canton, 1996; Vitousek et al., 1997; Sala et al., 2000). Concurrently with this global trend several new crustacean species have also been found in the Estonian coastal sea in recent years. The gammarid amphipod Gammarus tigrinus Sexton originates from the North American coast of the Atlantic Ocean. The species was introduced to Europe probably in ballast water and was first discovered in England in 1931 (Chambers, 1977). Although G. tigrinus was found in the Baltic Sea already in 1975, its significant range expansion started in the 1990s (Jazdzewski et al., 2002, 2005; Szaniawska et al., 2003). In the northern Baltic Sea G. tigrinus was first found in the northern Gulf of Riga (Herkul et al., 2006) and the northern Gulf of Finland in 2003 (Pienimaki et al., 2004). In 2005, G. tigrinus was found in the Neva Estuary, the easternmost part of the Gulf of Finland (Berezina, 2007). This species has caused a significant decrease in the diversity and density of native amphipods in the southern Baltic Sea (Grabowski et al., 2006) and Estonian coastal sea (Kotta et al., 2006; Orav-Kotta et al., 2009). The amphipod Chelicorophium curvispinum (Sars) originates from large rivers connected to the Black Sea and the Caspian Sea. It was found in the Baltic Sea already in the 1920s (Bij de Vaate et al., 2002). The species invaded to the Baltic and North seas through rivers and canals attached to the hulls of ships and in ballast water. Regardless of its long invasion history in the Baltic Sea, C. curvispinum was not found in the northern Baltic until 2005 when it was detected in the eastern part of the Estonian coast of the Gulf of Finland (Herkul & Kotta, 2007). In the next year, 2006, C. curvispinum was found in Luga Bay, Russia (Malyavin et al., 2008). Similarly to C. curvispinum, the gammarid amphipod Pontogammarus robustoides (Sars) originates from the lower reaches of Ponto-Caspian rivers and from brackish and freshwater lakes around the Black Sea (Bij de Vaate et al., 2002). In 1960-1961, the species was intentionally introduced into the Kaunas Water Reservoir on the Nemunas River, Lithuania (Bij de Vaate et al., 2002; Gumuliauskaite & Arbaciauskas, 2008). It successfully spread in the Nemunas drainage system including the Curonian Lagoon of the Baltic Sea. In 1999 P. robustoides was first found in Neva Bay, the easternmost part of the Gulf of Finland (Panov et al., 2003) and in 2006, in Lake Ladoga (Kurashov & Barbashova, 2008). In 2006 the species was recorded for the first time in the Estonian coastal sea. Similarly to G. tigrinus, P. robustoides has a potential to reduce the diversity and density of native gammarids (Panov et al., 2003; Gumuliauskaite & Arbaciauskas, 2008). The mysids Paramysis intermedia (Czerniavsky) and P. lacustris (Czerniavsky) are native to rivers connected to the Caspian Sea and Black Sea (Birshteina et al., 1968). In the 1970s P. lacustris and P. intermedia were introduced to Lake Peipsi but neither of the species has been sighted later (Timm et al., 2001). Both species were also introduced to Lake Vortsjarv, southern Estonia, in the 1970s, but only P. lacustris formed a permanent population there (Kangur et al., 2004). However, there is only a single record of P. lacustris in the Estonian coastal sea dating back to 1963 (Yarvekyulg, 1979). We are not aware of any successful introductions of P. intermedia in the Baltic Sea drainage area while P. lacustris inhabits the Curonian Lagoon, the southern Baltic Sea, already since the 1960s. In 2008 P. intermedia was found for the first time in the Baltic Sea. …\",\"PeriodicalId\":262667,\"journal\":{\"name\":\"Estonian Journal of Ecology\",\"volume\":\"1 1\",\"pages\":\"0\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2009-12-01\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"31\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Estonian Journal of Ecology\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.3176/ECO.2009.4.06\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Estonian Journal of Ecology","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.3176/ECO.2009.4.06","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 31

摘要

与栖息地丧失和气候变化一起,非本地物种的入侵是对全球生物多样性最严重的威胁之一。这种人为辅助的过程已经对非生物和生物环境产生了重大的、不可预测的和不可逆转的变化,并在世界范围内的各种水体中造成了严重的经济损失(例如Canton, 1996;Vitousek et al., 1997;Sala et al., 2000)。在这一全球趋势的同时,近年来在爱沙尼亚沿海海域也发现了几种新的甲壳类动物。双足类Gammarus tigrinus Sexton起源于大西洋的北美海岸。该物种可能是在压载水中被引入欧洲的,1931年在英国首次被发现(Chambers, 1977)。虽然早在1975年就在波罗的海发现了G. tigrinus,但其范围的显著扩张始于20世纪90年代(Jazdzewski et al., 2002, 2005;Szaniawska et al., 2003)。在波罗的海北部,首先在里加湾北部(Herkul et al., 2006)和2003年芬兰湾北部(Pienimaki et al., 2004)发现了G. tigrinus。2005年,在芬兰湾最东端的涅瓦河河口发现了G. tigrinus (Berezina, 2007)。该物种导致波罗的海南部(Grabowski et al., 2006)和爱沙尼亚沿海(Kotta et al., 2006)本地片脚类动物的多样性和密度显著下降;Orav-Kotta et al., 2009)。片足类弯螯虾(Chelicorophium curvispinum, Sars)起源于连接黑海和里海的大河。早在20世纪20年代,人们就在波罗的海发现了它(Bij de Vaate et al., 2002)。该物种通过附着在船体和压载水中的河流和运河入侵波罗的海和北海。尽管C. curvispinum在波罗的海有着悠久的入侵历史,但直到2005年在芬兰湾的爱沙尼亚海岸东部才在波罗的海北部被发现(Herkul & Kotta, 2007)。次年,2006年,C. curvispinum在俄罗斯Luga Bay被发现(Malyavin et al., 2008)。与C. curvispinum类似,gammarid片足类Pontogammarus robustoides (Sars)起源于里河下游以及黑海周围的咸淡水和淡水湖(Bij de Vaate et al., 2002)。1960-1961年,该物种被有意引入立陶宛Nemunas河上的Kaunas水库(Bij de Vaate et al., 2002;Gumuliauskaite & Arbaciauskas, 2008)。它成功地在Nemunas的排水系统中传播,包括波罗的海的库尔斯泻湖。1999年,在芬兰湾最东部的涅瓦湾首次发现了P. robustoides (Panov et al., 2003), 2006年在拉多加湖首次发现了P. robustoides (Kurashov & Barbashova, 2008)。2006年,该物种首次在爱沙尼亚沿海海域被记录下来。与G. tigrinus类似,P. robustoides有可能降低本地伽马虫的多样性和密度(Panov et al., 2003;Gumuliauskaite & Arbaciauskas, 2008)。米丝虫Paramysis intermedia (Czerniavsky)和P. lacustris (Czerniavsky)原产于连接里海和黑海的河流中(Birshteina et al., 1968)。在20世纪70年代,湖泊假鳗和中间假鳗被引入佩普斯湖,但这两个物种后来都没有被发现(Timm et al., 2001)。20世纪70年代,这两个物种也被引入到爱沙尼亚南部的Vortsjarv湖,但只有P. lacustris在那里形成了永久种群(Kangur et al., 2004)。然而,1963年以来,在爱沙尼亚沿海海域只有一个关于p.a laustris的记录(Yarvekyulg, 1979)。据我们所知,自20世纪60年代以来,在波罗的海流域还没有成功引进过中间假蝇,而湖泊假蝇已经栖息在波罗的海南部的库尔尼泻湖。2008年,在波罗的海首次发现了P. intermedia。…
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Crustacean invasions in the Estonian coastal sea
INTRODUCTION Together with habitat loss and climate change, invasions of nonindigenous species are one of the most serious threats to global biodiversity. This human-aided process has initiated significant, unpredictable, and irreversible changes to both the abiotic and the biotic environment and has caused severe economic damage in a variety of waterbodies worldwide (e.g. Canton, 1996; Vitousek et al., 1997; Sala et al., 2000). Concurrently with this global trend several new crustacean species have also been found in the Estonian coastal sea in recent years. The gammarid amphipod Gammarus tigrinus Sexton originates from the North American coast of the Atlantic Ocean. The species was introduced to Europe probably in ballast water and was first discovered in England in 1931 (Chambers, 1977). Although G. tigrinus was found in the Baltic Sea already in 1975, its significant range expansion started in the 1990s (Jazdzewski et al., 2002, 2005; Szaniawska et al., 2003). In the northern Baltic Sea G. tigrinus was first found in the northern Gulf of Riga (Herkul et al., 2006) and the northern Gulf of Finland in 2003 (Pienimaki et al., 2004). In 2005, G. tigrinus was found in the Neva Estuary, the easternmost part of the Gulf of Finland (Berezina, 2007). This species has caused a significant decrease in the diversity and density of native amphipods in the southern Baltic Sea (Grabowski et al., 2006) and Estonian coastal sea (Kotta et al., 2006; Orav-Kotta et al., 2009). The amphipod Chelicorophium curvispinum (Sars) originates from large rivers connected to the Black Sea and the Caspian Sea. It was found in the Baltic Sea already in the 1920s (Bij de Vaate et al., 2002). The species invaded to the Baltic and North seas through rivers and canals attached to the hulls of ships and in ballast water. Regardless of its long invasion history in the Baltic Sea, C. curvispinum was not found in the northern Baltic until 2005 when it was detected in the eastern part of the Estonian coast of the Gulf of Finland (Herkul & Kotta, 2007). In the next year, 2006, C. curvispinum was found in Luga Bay, Russia (Malyavin et al., 2008). Similarly to C. curvispinum, the gammarid amphipod Pontogammarus robustoides (Sars) originates from the lower reaches of Ponto-Caspian rivers and from brackish and freshwater lakes around the Black Sea (Bij de Vaate et al., 2002). In 1960-1961, the species was intentionally introduced into the Kaunas Water Reservoir on the Nemunas River, Lithuania (Bij de Vaate et al., 2002; Gumuliauskaite & Arbaciauskas, 2008). It successfully spread in the Nemunas drainage system including the Curonian Lagoon of the Baltic Sea. In 1999 P. robustoides was first found in Neva Bay, the easternmost part of the Gulf of Finland (Panov et al., 2003) and in 2006, in Lake Ladoga (Kurashov & Barbashova, 2008). In 2006 the species was recorded for the first time in the Estonian coastal sea. Similarly to G. tigrinus, P. robustoides has a potential to reduce the diversity and density of native gammarids (Panov et al., 2003; Gumuliauskaite & Arbaciauskas, 2008). The mysids Paramysis intermedia (Czerniavsky) and P. lacustris (Czerniavsky) are native to rivers connected to the Caspian Sea and Black Sea (Birshteina et al., 1968). In the 1970s P. lacustris and P. intermedia were introduced to Lake Peipsi but neither of the species has been sighted later (Timm et al., 2001). Both species were also introduced to Lake Vortsjarv, southern Estonia, in the 1970s, but only P. lacustris formed a permanent population there (Kangur et al., 2004). However, there is only a single record of P. lacustris in the Estonian coastal sea dating back to 1963 (Yarvekyulg, 1979). We are not aware of any successful introductions of P. intermedia in the Baltic Sea drainage area while P. lacustris inhabits the Curonian Lagoon, the southern Baltic Sea, already since the 1960s. In 2008 P. intermedia was found for the first time in the Baltic Sea. …
求助全文
通过发布文献求助,成功后即可免费获取论文全文。 去求助
来源期刊
自引率
0.00%
发文量
0
×
引用
GB/T 7714-2015
复制
MLA
复制
APA
复制
导出至
BibTeX EndNote RefMan NoteFirst NoteExpress
×
提示
您的信息不完整,为了账户安全,请先补充。
现在去补充
×
提示
您因"违规操作"
具体请查看互助需知
我知道了
×
提示
确定
请完成安全验证×
copy
已复制链接
快去分享给好友吧!
我知道了
右上角分享
点击右上角分享
0
联系我们:info@booksci.cn Book学术提供免费学术资源搜索服务,方便国内外学者检索中英文文献。致力于提供最便捷和优质的服务体验。 Copyright © 2023 布克学术 All rights reserved.
京ICP备2023020795号-1
ghs 京公网安备 11010802042870号
Book学术文献互助
Book学术文献互助群
群 号:604180095
Book学术官方微信