Rapid Establishment of the Alien Crab Rhithropanopeus Harrisii (Gould) in the Gulf of Riga/ Mudakrabi Rhithropanopeus Harrisii Kiire Naturaliseerumine Liivi Lahes

J. Kotta, H. Ojaveer
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引用次数: 35

Abstract

INTRODUCTION Owing to its low salinity and short evolutionary history, the Baltic Sea virtually lacks native top predatory crabs. This contrasts to true oceanic waters where crabs constitute an essential element of the nearshore benthic ecosystems (e.g. Lee, 1998). To date, the only 'iconic' species in the Baltic Sea range is the Chinese mitten crab Eriocheir sinensis (H. Milne-Edwards). Despite occasional findings of this invasive species all over the coastal Baltic Sea, the reproduction of the mitten crab in the central, northern, and eastern Baltic regions is considered unlikely due to the low salinity, and the individuals caught are assumed to have actively migrated into the region over 1500 km distance (Ojaveer et al., 2007). However, the Baltic Sea also hosts the Harris mud crab Rhithropanopeus harrisii (Gould) (Fig. 1). This species has a native distribution from New Brunswick (Canada) to Veracruz (Mexico). In Europe the invasive species was first found in 1874 in the Netherlands, in the Baltic Sea area it was first observed in 1936 (Nikolaev, 1951). In contrast to E. sinensis, the mud crab is capable of reproducing in the diluted Baltic Sea and can form high-density populations (Maiju Lehtiniemi, pers. comm.); thus, it may exert strong pressure on the local benthic macrophyte and invertebrate communities. Despite its long invasion history, until very recently the distribution of R. harrisii was confined to Mecklenburg Bay, the Oder Estuary, the Gulf of Gdansk, and the Curonian Lagoon only (Jazdzewski & Konopacka, 1993; Bacevicius & Gasiunaite, 2008; Czerniejewski, 2009; Jazdzewski & Grabowski, 2011). Seemingly, R. harrisii has a large between population variability in Europe with more recent populations showing a tendency for increased genetic diversity (Projecto-Garcia et al., 2010). This suggests that R. harrisii is still in the process of expansion in Europe and its sudden northwards expansion seems to be a result of new introductions. In this study we report the sudden expansion of this alien invasive species over 500 km northwards and provide information on its distribution. [FIGURE 1 OMITTED] MATERIAL AND METHODS Crabs are not systematically monitored in the Estonian coastal sea. Nevertheless, since 1995 the Estonian National Monitoring Programme surveys benthic macrophytes and the associated invertebrates around the whole Estonian coastal range. In addition, the programme also surveys pelagic communities. The phytobenthos and zooplankton sampling and sample analysis follow the guidelines developed for the HELCOM COMBINE programme (HELCOM, 2012). Although not specifically targeted towards large and mobile invertebrates, the national monitoring programme is potentially capable of sighting the mud crab both in benthic and pelagic ecosystems. In addition, there is another local long-term activity that provides semiquantitative data on crabs. Specifically, this is done through the provision of artificial spawning substrata for the commercially valuable fish pike-perch in Parnu Bay. This activity was started already in the late 1980s and has been done every year since then. Most of these artificial spawning substrata consist of linen gillnets of small mesh size. Such substratum may also provide a suitable habitat for the Harris mud crab and, therefore, may provide occurrence information on the species. These artificial spawning substrata were checked for the mud crab occurrence in 2011-2012, also with SCUBA diving, which was also performed in several additional localities in Parnu Bay to map the distribution of the species. Finally, owing to good long-term relations with local professional fishermen, several occurrence data on the crab were obtained from them. RESULTS AND DISCUSSION The Harris mud crab R. harrisii was first found in the Estonian waters in August 2011. Seven individuals were found in three deployed lines of pike-perch artificial spawning substrata at the northern coast of Parnu Bay (NE Gulf of Riga) (Fig. …
由于波罗的海盐度低,进化史短,几乎没有本土的顶级掠食性螃蟹。这与真正的海洋水域形成鲜明对比,螃蟹是近岸底栖生态系统的基本组成部分(例如Lee, 1998)。迄今为止,波罗的海地区唯一的“标志性”物种是中华绒螯蟹(h.m ilne- edwards)。尽管在波罗的海沿岸偶尔发现这种入侵物种,但由于盐度低,在波罗的海中部、北部和东部地区不太可能繁殖大闸蟹,并且捕获的个体被认为已经主动迁移到1500公里以外的地区(Ojaveer et al., 2007)。然而,波罗的海也栖息着哈里斯泥蟹Rhithropanopeus harrisii (Gould)(图1)。该物种在加拿大新不伦瑞克省到墨西哥韦拉克鲁斯州的本地分布。在欧洲,这种入侵物种于1874年在荷兰首次被发现,1936年在波罗的海地区首次被观察到(Nikolaev, 1951)。与中华赤潮蟹相比,泥蟹能够在稀释的波罗的海繁殖,并能形成高密度种群(Maiju Lehtiniemi, pers。通讯);因此,它可能对当地的底栖植物和无脊椎动物群落产生强大的压力。尽管其入侵历史悠久,但直到最近,R. harrisii的分布仅限于梅克伦堡湾、奥得河口、格但斯克湾和库尔潟湖(Jazdzewski & Konopacka, 1993;Bacevicius & Gasiunaite, 2008;Czerniejewski, 2009;Jazdzewski & Grabowski, 2011)。从表面上看,harrisii在欧洲具有较大的种群间变异性,最近的种群表现出遗传多样性增加的趋势(Projecto-Garcia et al., 2010)。这表明harrisii在欧洲仍处于扩张过程中,其突然向北扩张似乎是新引进的结果。在这项研究中,我们报告了这种外来入侵物种突然向北扩展超过500公里,并提供了其分布信息。材料和方法在爱沙尼亚沿海海域没有对螃蟹进行系统监测。然而,自1995年以来,爱沙尼亚国家监测方案调查了整个爱沙尼亚沿海地区的底栖大型植物和相关的无脊椎动物。此外,该方案还调查了远洋群落。底栖植物和浮游动物取样和样本分析遵循HELCOM联合项目制定的指导方针(HELCOM, 2012年)。虽然不是专门针对大型和可移动的无脊椎动物,但国家监测方案有可能在底栖和远洋生态系统中发现泥蟹。此外,还有另一项本地长期活动,提供有关螃蟹的半定量数据。具体来说,这是通过为帕尔努湾具有商业价值的鱼梭鲈提供人工产卵基质来实现的。这项活动早在20世纪80年代末就开始了,此后每年都进行。这些人工产卵基质大多由小网目尺寸的亚麻刺网组成。这种基质也可能为哈里斯泥蟹提供合适的栖息地,因此可能提供该物种的发生信息。2011年至2012年期间,研究人员通过水肺潜水检查了这些人工产卵基质中泥蟹的出现情况,并在帕尔努湾的其他几个地方进行了测试,以绘制该物种的分布。最后,由于与当地专业渔民的长期良好关系,从他们那里获得了一些蟹的发生数据。结果与讨论哈里斯泥蟹于2011年8月首次在爱沙尼亚水域被发现。在帕尔努湾北部海岸(里加湾东北部)的三条梭鲈人工产卵基质中发现了7只梭鲈(图. ...)
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