Norton J, Rollinson D, Lewis J W
School of Biological Sciences, Royal Holloway, University of London, Egham, Surrey TW20 0EX.
Parasitology. 2005 Jun;130(Pt 6):679-86. doi: 10.1017/s0031182004007139.
European eels Anguilla anguilla from the rivers Thames and Test, in the south of England, were examined between 2000 and 2003 for infection with the swim-bladder nematode Anguillicola crassus. Since its introduction to Thames eels at tidal estuarine locations circa 1987, A. crassus has become established in non-tidal freshwater stretches upriver and data from these locations are reported for the first time. The prevalence of infection at Thames estuary locations was higher during 2000-2003 than for the period 1987-1992. By 2003, similar prevalences were observed at freshwater and estuarine locations, but infection intensities were significantly higher in freshwater. Eels from the river Test appear to have been recently colonized by A. crassus (circa 2000). Parasite population establishment within these eels was uncharacteristically slow during 2000-2001, with low prevalence and intensity of infection, and few gravid females during this period. By 2003, infection levels in Test eels were similar to those in Thames eels. The expansion of the A. crassus population in Test eels has occurred in the absence of the paratenic host ruffe Gymnocephalus cernuus, and at suboptimal pH for the survival and infectivity of free-living larvae. The epidemiology of A. crassus in Test eels demonstrates that transmission of A. crassus by ruffe is not required for high prevalence and intensity of infection in eels. However, the consistently low and atypical levels of infection in Test eels during 2000 and 2001 suggests that paratenic transmission by ruffe may provide a substantial contribution to the dynamics of A. crassus in eels in the early years following introduction, by facilitating the rapid increase in prevalence and intensity of A. crassus infection that typically occurs during this time.
2000年至2003年间,对来自英格兰南部泰晤士河和泰斯特河的欧洲鳗鲡(Anguilla anguilla)进行了检查,以确定其是否感染了鳔线虫(Anguillicola crassus)。自1987年左右在潮汐河口地区引入泰晤士河鳗鱼以来,粗厚鳗鲡已在上游非潮汐淡水河段定居,本文首次报告了这些地点的数据。2000年至2003年期间,泰晤士河河口地区的感染率高于1987年至1992年期间。到2003年,淡水和河口地区的感染率相似,但淡水中的感染强度明显更高。泰斯特河的鳗鱼似乎最近(约2000年)被粗厚鳗鲡定植。在2000年至2001年期间,这些鳗鱼体内寄生虫种群的建立异常缓慢,感染率和感染强度较低,且在此期间很少有怀孕的雌虫。到2003年,泰斯特河鳗鱼的感染水平与泰晤士河鳗鱼相似。在没有中间宿主梅花鲈(Gymnocephalus cernuus)且自由生活幼虫的生存和感染性处于非最适pH值的情况下,泰斯特河鳗鱼体内的粗厚鳗鲡种群仍在扩张。粗厚鳗鲡在泰斯特河鳗鱼中的流行病学表明,鳗鱼中高感染率和高感染强度并不需要梅花鲈来传播粗厚鳗鲡。然而,2000年和2001年泰斯特河鳗鱼中持续较低且非典型的感染水平表明,在引入后的最初几年,梅花鲈的中间传播可能通过促进粗厚鳗鲡感染率和感染强度的快速增加,对粗厚鳗鲡在鳗鱼中的动态变化做出了重大贡献,而这种快速增加通常在此期间发生。