Neal Alexandra E, Moore Paul A
Laboratory for Sensory Ecology, Department of Biological Sciences, Bowling Green State University, Bowling Green, OH 43403, USA; University of Michigan Biological Station, 9133 Biological Road, Pellston, MI 49769, USA.
Laboratory for Sensory Ecology, Department of Biological Sciences, Bowling Green State University, Bowling Green, OH 43403, USA; University of Michigan Biological Station, 9133 Biological Road, Pellston, MI 49769, USA.
Ecotoxicol Environ Saf. 2017 Jan;135:347-357. doi: 10.1016/j.ecoenv.2016.10.015. Epub 2016 Oct 20.
Animals living in aquatic habitats regularly encounter anthropogenic chemical pollution. Typically, the toxicity of a chemical toxicant is determined by the median lethal concentration (LC) through a static exposure test. However, LC values and static tests do not provide an accurate representation of exposure to pollutants within natural stream systems. In their native habitats, animals experience exposure as a fluctuating concentration due to turbulent mixing, temporal variations of contamination (seasonal inputs), and contaminant input type (point vs. non-point). Research has shown that turbulent environments produce exposures with a high degree of fluctuation in frequency, duration, and intensity. In order to more effectively evaluate the effects of pollutants, we created a dynamic exposure paradigm, utilizing both flow and substrate within a small mesocosm. A commonly used pharmaceutical, naproxen, was used as the toxicant and female crayfish (Orconectes virilis) as the target organism to investigate changes in fighting behavior as a result of dynamic exposure. Crayfish underwent either a 23h long static or a dynamic exposure to naproxen. Following exposure, the target crayfish and an unexposed size matched opponent underwent a 15min fight trial. These fight trials were recorded and later analyzed using a standard ethogram. Results indicate that exposure to sublethal concentrations of naproxen, in both static and flowing conditions, negatively impact aggressive behavior. Results also indicate that a dynamic exposure paradigm has a greater negative impact on behavior than a static exposure. Turbulence and habitat structure play important roles in shaping chemical exposure. Future research should incorporate features of dynamic chemical exposure in order to form a more comprehensive image of chemical exposure and predict the resulting sublethal effects from exposure. Possible techniques for assessment include utilizing flow-through experimental set-ups in tandem with behavioral or physiological endpoints as opposed to acute toxicity. Other possibilities of assessment could involve utilizing fine-scale chemical measurements of pollutants to determine the actual concentrations animals encounter during an exposure event.
生活在水生栖息地的动物经常会遇到人为化学污染。通常,化学毒物的毒性是通过静态暴露试验,由半数致死浓度(LC)来确定的。然而,LC值和静态试验并不能准确反映自然溪流系统中污染物的暴露情况。在其原生栖息地,由于湍流混合、污染的时间变化(季节性输入)以及污染物输入类型(点源与非点源),动物所经历的暴露浓度是波动的。研究表明,湍流环境会产生频率、持续时间和强度高度波动的暴露。为了更有效地评估污染物的影响,我们在一个小型中宇宙中利用水流和基质创建了一种动态暴露模式。一种常用药物萘普生被用作毒物,雌性小龙虾(奥氏原螯虾)作为目标生物,以研究动态暴露导致的战斗行为变化。小龙虾接受了长达23小时的萘普生静态或动态暴露。暴露后,目标小龙虾与一只未暴露的大小匹配的对手进行了15分钟的战斗试验。这些战斗试验被记录下来,随后使用标准行为图谱进行分析。结果表明,在静态和流动条件下,暴露于亚致死浓度的萘普生都会对攻击行为产生负面影响。结果还表明,动态暴露模式对行为的负面影响比静态暴露更大。湍流和栖息地结构在塑造化学暴露方面起着重要作用。未来的研究应纳入动态化学暴露的特征,以便形成更全面的化学暴露图景,并预测暴露产生的亚致死效应。可能的评估技术包括将流通式实验装置与行为或生理终点结合使用,而不是急性毒性。其他评估可能性可能包括利用污染物的精细化学测量来确定动物在暴露事件中实际遇到的浓度。