U.S. Geological Survey Columbia Environmental Research Center, 4200 New Haven Road, Columbia, MO 65201, USA.
U.S. Geological Survey Southwest Isotope Research Laboratories, Denver Federal Center, MS 963, Denver, CO 80225, USA.
Sci Total Environ. 2021 May 15;769:144714. doi: 10.1016/j.scitotenv.2020.144714. Epub 2021 Jan 20.
Aquatic insects link food web dynamics across freshwater-terrestrial boundaries and subsidize terrestrial consumer populations. Contaminants that accumulate in larval aquatic insects and are retained across metamorphosis can increase dietary exposure for riparian insectivores. To better understand potential exposure of terrestrial insectivores to aquatically-derived trace metals, metal concentrations in water and tissues were analyzed from different components of streams and riparian food webs across a large (2-3 orders of magnitude) metal gradient (e.g., Zn, Cu, Cd, Pb) in the Rocky Mountains (USA). Our research indicates that the trace metal concentration gradient present among streams was lost during metamorphosis of aquatic larval insects into terrestrially flying adults, decoupling terrestrial exposures from aquatic concentrations. This pattern was caused by declines in 1) among-stream variation in trace metal concentrations, 2) relationships between metal concentrations in paired water and food web components, and 3) mean metal concentrations within aquatic food webs and across the aquatic-terrestrial boundary. Specifically, among-stream variation in trace metal concentrations was highest for water and aquatic vegetation, intermediate for aquatic insect larvae (30% lower than water) and lowest for adult aquatic insects and riparian spiders (65% lower). Metal concentrations in paired water and food web components ranged from highly related across the stream-metal gradient (slopes 1) for water and aquatic vegetation, to less related (slopes closer to 0) for aquatic vegetation and aquatic insect larvae, to unrelated (slopes ~0) for aquatic larval and adult insects. Finally, mean metal concentrations were highest in aquatic vegetation and lowest in adult aquatic insects emerging from streams (50% lower than aquatic vegetation). Our results indicate less efficient trophic transfer and higher metamorphic loss of trace metals from high metal streams (i.e., exposure-dependent transfer). For many trace metals, aquatic-terrestrial dietary transfer is unlikely to be an important source of exposure for terrestrial insectivores of adult aquatic insects.
水生昆虫将食物网动态联系在淡水-陆地边界,并为陆地消费者群体提供食物。在幼虫阶段积累并在变态过程中保留的污染物会增加河岸食虫动物的饮食暴露量。为了更好地了解陆地食虫动物对水生衍生痕量金属的潜在暴露,我们分析了落矶山脉(美国)不同溪流和河岸食物网成分中的水和组织中的金属浓度,这些成分跨越了一个大的(2-3 个数量级)金属梯度(例如 Zn、Cu、Cd、Pb)。我们的研究表明,在水生幼虫昆虫变态为陆地飞行成虫的过程中,溪流之间存在的痕量金属浓度梯度消失了,使陆地暴露与水浓度脱钩。这种模式是由以下原因造成的:1)溪流之间痕量金属浓度的变化;2)配对水和食物网成分之间金属浓度的关系;3)水生食物网内和水生-陆地边界内的平均金属浓度。具体来说,痕量金属浓度的溪流间变化在水中最高,在水生植被中次之,在水生昆虫幼虫中(比水低约 30%)最低,在成年水生昆虫和河岸蜘蛛中(比水低约 65%)最低。配对水和食物网成分的金属浓度从溪流金属梯度上高度相关(斜率约为 1),从水和水生植被到水生植被和水生昆虫幼虫的关系不太相关(斜率更接近 0),到水生幼虫和成年昆虫的关系不相关(斜率约为 0)。最后,平均金属浓度在水生植被中最高,在从溪流中出现的成年水生昆虫中最低(比水生植被低约 50%)。我们的结果表明,从高金属溪流中,痕量金属的营养转移效率较低,且变态损失较高(即暴露依赖性转移)。对于许多痕量金属来说,水生-陆地饮食转移不太可能成为成年水生昆虫的陆地食虫动物的重要暴露源。