Vigneron A, Geffard O, Coquery M, François A, Quéau H, Chaumot A
Irstea, UR MALY Milieux aquatiques, écologie et pollutions, Centre de Lyon-Villeurbanne, 5 rue de la doua - CS70077, 69626, Villeurbanne, France.
Ecotoxicology. 2015 Aug;24(6):1239-49. doi: 10.1007/s10646-015-1491-z. Epub 2015 May 24.
Deciphering evolutionary processes occurring within long-term contaminated wild populations is essential for the ecological risk assessment of persistent chemical contaminations. Using field populations of Gammarus, a commonly-used genus in aquatic ecotoxicology, the present study sought to gain insights into the extent to which long-term exposure to metals in the field could effectively lead to shifts in toxicological sensitivities. For this, we identified a Gammarus population inhabiting a stream contaminated by cadmium (Cd). We compared the Cd-exposure and Cd-sensitivity of this population to those of five reference populations. Active biomonitoring determined in different years and seasons that significant levels of Cd were bioavailable in the contaminated site. Laboratory sensitivity tests under common garden conditions established that this long-term field exposure led to the development of a moderate Cd tolerance, which was maintained after a 3-week acclimatization in the laboratory, and transmitted to offspring produced under clean conditions. The potential physiological costs of tolerance were assessed by means of feeding rate measurements (in the laboratory and in situ). They revealed that, unlike for reference populations, the feeding activity of organisms from the tolerant population was greatly decreased when they were maintained under laboratory conditions, potentially indicating a high population vulnerability to environmental perturbations. Because dissolved Cd concentrations in water from the contaminated site were low (averaging 0.045 µg L(-1)) and below the current European environmental quality standard for Cd for inland surface waters (fixed at 0.08 µg L(-1) in soft water environments), this case study sheds light onto the extent to which current environmental quality standards are protective against potential adverse outcomes of adaptive and micro-evolutionary processes occurring in contaminated environments.
解读长期受污染的野生种群中发生的进化过程对于持久性化学污染物的生态风险评估至关重要。本研究以水生生态毒理学中常用的钩虾属野外种群为研究对象,旨在深入了解野外长期接触金属能在多大程度上有效导致毒理学敏感性的转变。为此,我们确定了一个栖息在受镉(Cd)污染溪流中的钩虾种群。我们将该种群的镉暴露情况和对镉的敏感性与五个参照种群进行了比较。通过在不同年份和季节进行的活性生物监测确定,受污染场地中镉的生物可利用水平显著。在共同园圃条件下进行的实验室敏感性测试表明,这种长期的野外暴露导致了中等程度的镉耐受性的形成,在实验室经过3周的驯化后这种耐受性依然存在,并传递给在清洁条件下产生的后代。通过测量摄食率(在实验室和原位)评估了耐受性的潜在生理成本。结果显示,与参照种群不同,耐受性种群的生物在实验室条件下饲养时摄食活动大幅下降,这可能表明该种群对环境扰动的脆弱性较高。由于受污染场地水体中的溶解镉浓度较低(平均为0.045 μg L⁻¹),低于当前欧洲内陆地表水镉的环境质量标准(在软水环境中定为0.08 μg L⁻¹),本案例研究揭示了当前环境质量标准在多大程度上能够保护免受污染环境中发生的适应性和微进化过程的潜在不利影响。