Department of Environmental Sciences and Lake Erie Center, University of Toledo, 6200 Bay Shore Rd, Oregon, OH, USA; Darrin Fresh Water Institute, Department of Biological Sciences, Rensselaer Polytechnic Institute, Troy, New York, USA.
Darrin Fresh Water Institute, Department of Biological Sciences, Rensselaer Polytechnic Institute, Troy, New York, USA; Department of Biology, Montclair State University, Montclair, NJ, USA.
Sci Total Environ. 2019 Dec 1;694:133704. doi: 10.1016/j.scitotenv.2019.133704. Epub 2019 Jul 31.
Non-native species often lead to undesirable ecological and environmental impacts. Two hypotheses that predict establishment of non-native species are enemy release and biotic resistance. Support for these hypotheses in freshwater invasions is mixed. Experiments combined with field observations provide a complementary approach to understanding how interactions between native and non-native species lead to enemy release or biotic resistance. We tested experimentally whether these hypotheses provided insights into the invasion of the banded mystery snail (Viviparus georgianus), which has invaded the Great Lakes region and northeastern Unites States (US) from the southeastern US. Because freshwater systems vary widely in their nutrient concentrations due to natural and anthropogenic processes, we tested whether nutrient additions altered competitive and predatory interactions that regulate mechanisms of enemy release or biotic resistance. We evaluated the status of the mystery snail invasion in a 3-year field survey of Lake George (NY, US) to identify if field observations supported any experimental conclusions. The presence of the banded mystery snail led to a 14% and 27% reduction in biomass of a native competitor under low- and high-nutrient concentrations, respectively. The mystery snail also triggered a 29% biomass loss of a native snail predator, but only in low-nutrient concentrations. Field surveys indicated that the mystery snail dominated the snail community; of seven snail species, it comprised 77% of all snails. Results from the field surveys combined with experimental results indicate that neither competitors nor predators have likely suppressed the invasion of the banded mystery snail. This conclusion is consistent with competitive- and predatory-enemy release as we found no indication of biotic resistance via competition or predation from native species. Our results further highlight that the post-establishment impacts of invasive species are altered by the trophic state of freshwater ecosystems.
非本地物种通常会对生态和环境产生不良影响。有两个假说可以预测非本地物种的定殖,即天敌释放和生物阻力。这两个假说在淡水入侵中的支持程度是混合的。实验与野外观察相结合,为理解本地和非本地物种之间的相互作用如何导致天敌释放或生物阻力提供了一种互补的方法。我们通过实验测试了这些假说是否有助于理解带纹神秘螺(Viviparus georgianus)的入侵,这种螺已经从美国东南部入侵到大湖区和美国东北部。由于淡水系统由于自然和人为过程,其养分浓度差异很大,我们测试了养分添加是否改变了调节天敌释放或生物阻力机制的竞争和捕食相互作用。我们通过对乔治湖(纽约州,美国)的 3 年野外调查评估了神秘螺的入侵状况,以确定野外观察是否支持任何实验结论。带纹神秘螺的存在导致在低养分和高养分浓度下,本地竞争者的生物量分别减少了 14%和 27%。神秘螺还导致一种本地蜗牛捕食者的生物量损失了 29%,但仅在低养分浓度下。野外调查表明,神秘螺主导了蜗牛群落;在七个蜗牛物种中,它占所有蜗牛的 77%。野外调查结果与实验结果相结合表明,竞争和捕食者都没有可能抑制带纹神秘螺的入侵。这一结论与竞争和捕食天敌释放一致,因为我们没有发现来自本地物种的竞争或捕食对生物阻力的任何迹象。我们的研究结果进一步强调,入侵物种的建立后影响会被淡水生态系统的营养状态所改变。