van der Gaag Marinus, van der Velde Gerard, Wijnhoven Sander, Leuven Rob S E W
Department of Animal Ecology and Physiology, Institute for Water and Wetland Research, Radboud University Nijmegen, Heyendaalseweg 135, 6525 AJ Nijmegen, The Netherlands.
Department of Animal Ecology and Physiology, Institute for Water and Wetland Research, Radboud University Nijmegen, Heyendaalseweg 135, 6525 AJ Nijmegen, The Netherlands ; Naturalis Biodiversity Center, P.O. 9517, 2300 RA Leiden, The Netherlands ; Netherlands Centre of Expertise for Exotic Species (NEC-E), Heyendaalseweg 135, 6525 AJ Nijmegen, The Netherlands.
Mar Biol. 2016;163:147. doi: 10.1007/s00227-016-2926-7. Epub 2016 Jun 9.
The benthic stages of Dreissenidae and Mytilidae may be dispersed over long distances while attached to ship hulls. Alternatively, larvae may be transported by water currents and in the ballast and bilge water of ships and vessels. To gain insight into dispersal potential and habitat suitability, survival of the benthic stages of two invasive dreissenid species ( and ) and one mytilid species () chosen based on their occurrence in fresh, brackish and sea water, respectively, were tested in relation to salinity. They were exposed to various salinities in mesocosms during three long-term experiments at outdoor temperatures. Mussel survival was studied without prior acclimation, reflecting conditions experienced when attached to ship hulls while travelling along a salinity gradient from fresh or brackish water to sea water, or vice versa. Initially, mussels react to salinity shock by temporarily closing their valves, suspending ventilation and feeding. However, this cannot be maintained for long periods and adaptation to higher salinity must eventually occur. Bivalve survival was monitored till the last specimen of a test cohort died. The results of the experiments allowed us to distinguish favorable (f.: high tolerance) and unfavorable (u.: no or low tolerance) salinity ranges in practical salinity units (PSU) for each species, viz. for 0.2-6.0 PSU (f.), 7.0-30.0 PSU (u.), for 0.2-17.5 PSU (f.), 20.0-30.0 PSU (u.) and for 10.5-36.0 PSU (f.), 0.2-9.0 and 40 PSU (u.). At the unfavorable salinities, all mussels died within 14 days of initial exposure with the exception of (23-30 days). The maximum duration of survival of single specimens of was 318 days at a salinity of 3.2 PSU, of 781 days at 15.0 PSU and of 1052 days at 15.0 PSU. The number of days survived was compared with the duration of actual ship voyages to estimate the real world survival potentials of species dependent of salinity changes, travel distances and durations. The conclusion is that salinity shocks during the trip were survived within the favorable salinity range but that the species tolerate only for a few weeks the unfavorable salinity range. This functions as a barrier for dispersal. However, at faster and more frequent shipping in the future salinity can become no longer very important as a dispersal barrier.
Dreissenidae科和Mytilidae科的底栖阶段可能在附着于船体时远距离扩散。或者,幼虫可能通过水流以及船舶的压舱水和舱底水进行运输。为了深入了解扩散潜力和栖息地适宜性,基于它们分别出现在淡水、咸淡水和海水中的情况,选择了两种入侵的Dreissenidae科物种(和)以及一种Mytilidae科物种()的底栖阶段,针对盐度进行了生存测试。在三个室外温度下的长期实验中,它们被置于中宇宙中,暴露于各种盐度环境。研究了贻贝在未事先适应的情况下的生存情况,这反映了附着在船体上沿盐度梯度从淡水或咸淡水到海水,或反之亦然移动时所经历的条件。最初,贻贝会通过暂时关闭瓣膜、暂停通气和进食来应对盐度冲击。然而,这种情况无法长期维持,最终必须适应更高的盐度。监测双壳类动物的生存情况,直到测试群体中的最后一个标本死亡。实验结果使我们能够区分每个物种在实际盐度单位(PSU)下的适宜(f.:高耐受性)和不适宜(u.:无或低耐受性)盐度范围,即对于,0.2 - 6.0 PSU(适宜),7.0 - 30.0 PSU(不适宜);对于,0.2 - 17.5 PSU(适宜),20.0 - 30.0 PSU(不适宜);对于,10.5 - 36.0 PSU(适宜),0.2 - 9.0和40 PSU(不适宜)。在不适宜的盐度下,除了(23 - 30天)外,所有贻贝在初次暴露后的14天内死亡。在3.2 PSU盐度下,单个的最长存活时间为318天;在15.0 PSU盐度下,的最长存活时间为781天;在15.0 PSU盐度下,的最长存活时间为1052天。将存活天数与实际船舶航行持续时间进行比较,以估计依赖于盐度变化、航行距离和持续时间的物种在现实世界中的生存潜力。结论是,航行过程中的盐度冲击在适宜盐度范围内可以承受,但这些物种在不适宜盐度范围内只能耐受几周时间。这成为了扩散的障碍。然而,在未来更快且更频繁的航运情况下,盐度作为扩散障碍可能不再非常重要。