Laboratory for Sensory Ecology, Department of Biological Sciences, J.P. Scott Center for Neuroscience, Mind, and Behavior, Bowling Green State University, Bowling Green, OH, 43403, USA.
University of Michigan Biological Station, 9133 Biological Road, Pellston, MI, 49769, USA.
Arch Environ Contam Toxicol. 2018 Apr;74(3):372-394. doi: 10.1007/s00244-017-0444-3. Epub 2017 Sep 5.
In flowing systems, fluctuations in the frequency, magnitude, and duration of exposure occurs due to turbulence and geomorphology, causing spatial and temporal variations in chemical exposure at the scale of the organism. Spatial models representing toxicant distribution at the appropriate scales of stream organisms are noticeably missing from the literature. To characterize the fine scale distribution of pollutants in freshwater streams at the scale of a benthic organism, nine artificial stream habitats were created (riffle, pool, run, bend, woody debris) with either sand or gravel substrate. Dopamine was released as a chemical tracer, mimicking a groundwater source, and measurements were recorded with a microelectrode and Epsilon electrochemical recording system. Proxies for the frequency, magnitude, and duration of chemical exposure were extracted. Geographic information systems and an inverse distance weight interpolation technique were used to predict spatially the chemical distribution throughout the habitats. Spatial and temporal variations of exposure were exhibited within and across habitats, indicating that the frequency, magnitude, and duration of exposure is influenced by the organism's location within a habitat and the habitat it resides in. The run and pool with sand substrate contained the greatest frequency, magnitude, and duration of exposure, suggesting a more detrimental exposure compared to other habitats. Differences in peak heights within and across habitats are orders of magnitude in value. Spatial and temporal fluctuations of fine scale exposure need to be considered in both ecotoxicology and water quality modeling to represent and understand the exposure of pollutants impacting benthic organisms.
在流动系统中,由于紊流和地貌的原因,暴露的频率、幅度和持续时间会发生波动,导致生物体尺度上的化学暴露存在时空变化。在文献中明显缺少代表生物体适当尺度上有毒物质分布的空间模型。为了描述淡水溪流中污染物在底栖生物尺度上的精细分布,用沙或砾石作为基质创建了九个人工溪流生境(急流、水池、流段、弯道、木本碎屑)。多巴胺作为示踪剂被释放出来,模拟地下水源,并用微电极和 Epsilon 电化学记录系统进行测量。提取了化学暴露的频率、幅度和持续时间的代理变量。地理信息系统和反距离权重插值技术被用于预测整个生境中化学物质的空间分布。暴露的时空变化在生境内部和生境之间都有表现,表明暴露的频率、幅度和持续时间受到生物体在生境中的位置和它所在生境的影响。沙基质的急流和水池中含有最大频率、幅度和持续时间的暴露,这表明与其他生境相比,暴露更具危害性。在生境内部和生境之间,峰值高度的差异在数量级上是不同的。在生态毒理学和水质模型中都需要考虑精细尺度暴露的时空波动,以代表和理解影响底栖生物的污染物的暴露。