Ward J L, Korn V, Auxier A N, Schoenfuss H L
Department of Biology, Ball State University, 2111 W Riverside Ave, Muncie, IN 47306, USA.
Aquatic Toxicology Laboratory, Department of Biology, St. Cloud State University, 720 4th Avenue South, St Cloud, MN 56301, USA.
Integr Org Biol. 2020 Apr 1;2(1):obaa008. doi: 10.1093/iob/obaa008. eCollection 2020.
A variety of environmental estrogens are commonly detected in human-impacted waterways. Although much is known about the effects of these environmental estrogens on the reproductive physiology and behavior of individuals within species, comparatively less is known about how these compounds alter the outcomes of interactions between species. Furthermore, few studies have considered how the effects of contaminants are modulated by natural variation in abiotic factors, such as temperature. To help fill this knowledge gap, we conducted a factorial experiment to examine the independent and combined effects of estrone (E1) and temperature on the outcome of predator-prey interactions between two common North American freshwater fishes, fathead minnows () and bluegill sunfish (). Larval fathead minnows and adult sunfish were exposed to either a low (mean±standard deviation, 90.1 ± 18 ng/L; = 16) or high (414 ± 147 ng/L; = 15) concentration of E1 or to a solvent control for 30 days at one of four natural seasonal temperatures (15°C, 18°C, 21°C, and 24°C) before predation trials were performed. Exposure to E1 was associated with a significant increase in larval predation mortality that was independent of temperature. Across all temperature treatments, approximately 74% of control minnows survived; this survivorship significantly exceeded that of minnows exposed to either concentration of E1 (49% and 53% for minnows exposed to the low and high concentrations, respectively). However, exposure to E1 also impaired the prey-capture success of sunfish, partially mitigating predation pressure on exposed minnows. Overall prey-capture success by sunfish showed an inverted U-shaped distribution with temperature, with maximal prey consumption occurring at 21°C. This study illustrates the vulnerability of organismal interactions to estrogenic pollutants and highlights the need to include food web interactions in assessments of risk.
在受人类活动影响的水道中,通常能检测到多种环境雌激素。尽管人们对这些环境雌激素对物种内个体生殖生理和行为的影响了解很多,但对于这些化合物如何改变物种间相互作用的结果,了解相对较少。此外,很少有研究考虑污染物的影响是如何受到非生物因素(如温度)的自然变化调节的。为了填补这一知识空白,我们进行了一项析因实验,以研究雌酮(E1)和温度对北美两种常见淡水鱼——黑头呆鱼(Pimephales promelas)和蓝鳃太阳鱼(Lepomis macrochirus)之间捕食者 - 猎物相互作用结果的独立和综合影响。在进行捕食试验之前,将黑头呆鱼幼鱼和成体太阳鱼在四个自然季节温度(15°C、18°C、21°C和24°C)之一的条件下,暴露于低浓度(平均值±标准差,90.1 ± 18 ng/L;n = 16)或高浓度(414 ± 147 ng/L;n = 15)的E1或溶剂对照中30天。暴露于E1与幼鱼捕食死亡率的显著增加相关,且与温度无关。在所有温度处理中,约74%的对照呆鱼存活;这一存活率显著超过暴露于任何一种E浓度的呆鱼(暴露于低浓度和高浓度的呆鱼存活率分别为49%和53%)。然而,暴露于E1也损害了太阳鱼的猎物捕获成功率,部分减轻了对暴露呆鱼的捕食压力。太阳鱼的总体猎物捕获成功率随温度呈倒U形分布,最大猎物消耗量出现在21°C。这项研究说明了生物相互作用对雌激素污染物的脆弱性,并强调了在风险评估中纳入食物网相互作用的必要性。