Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences, Sweden.
WasserCluster - Biologische Station Lunz, Inter-University Center for Aquatic Ecosystem Research, Lunz am See, Austria.
Sci Total Environ. 2019 Jun 15;669:821-832. doi: 10.1016/j.scitotenv.2019.03.171. Epub 2019 Mar 13.
Dietary uptake is a key step in conveying both toxic mercury (Hg; particularly as highly bioavailable methylmercury, MeHg) and essential dietary biochemicals, such as polyunsaturated fatty acids (PUFA), across trophic levels within aquatic food webs. Using stable isotopes and fatty acids we evaluated the role of food sources in size-fractioned plankton and littoral macroinvertebrates for the bioaccumulation of total Hg and MeHg in six oligotrophic and one mesotrophic Swedish lakes with differing concentrations of dissolved organic carbon (DOC). We found that the consumption of both algal and terrestrial diets (assessed by PUFA and long-chain saturated fatty acids, respectively) predicted >66% of the Hg concentration variability in meso- (100-500 μm) and macrozooplankton (>500 μm) in oligotrophic lakes. In the mesotrophic lake, total Hg bioaccumulation in higher trophic level biota, carnivorous macroinvertebrates was also significantly related to terrestrial diet sources (R = 0.65, p < 0.01). However, lake pH and DOC correlated to total Hg bioaccumulation and bioconcentration across all lakes, suggesting the consumption of different diet sources is mediated by the influence of lake characteristics. This field study reveals that using dietary biomarkers (stable isotopes and fatty acids) together with the physico-chemical lake parameters pH and nutrients together improve our ability to predict Hg bioaccumulation in aquatic food webs. Fatty acids used as dietary biomarkers provide correlative evidence of specific diet source retention in consumers and their effect on Hg bioaccumulation, while pH and nutrients are the underlying physico-chemical lake parameters controlling differences in Hg bioaccumulation between lakes.
饮食摄入是在水生食物网的营养级之间传递有毒汞(Hg;尤其是具有高生物可利用性的甲基汞,MeHg)和必需的饮食生物化学物质(如多不饱和脂肪酸,PUFA)的关键步骤。我们使用稳定同位素和脂肪酸来评估食物来源在大小分级浮游生物和沿岸大型无脊椎动物中对总汞和 MeHg 生物积累的作用,这些浮游生物和大型无脊椎动物来自于 6 个贫营养和 1 个中营养的瑞典湖泊,这些湖泊的溶解有机碳(DOC)浓度不同。我们发现,藻类和陆地饮食的消耗(分别通过 PUFA 和长链饱和脂肪酸来评估)可以解释贫营养湖泊中中型(100-500 μm)和大型浮游动物(>500 μm)中汞浓度变异性的>66%。在中营养湖泊中,较高营养级生物(肉食性大型无脊椎动物)的总汞生物积累也与陆地饮食来源显著相关(R=0.65,p<0.01)。然而,在所有湖泊中,总汞的生物积累和浓缩都与湖的 pH 值和 DOC 相关,这表明不同的饮食来源的消耗是由湖的特征所调节的。这项实地研究表明,使用饮食生物标志物(稳定同位素和脂肪酸)以及 pH 值和营养等理化湖参数,可以提高我们预测水生食物网中汞生物积累的能力。脂肪酸作为饮食生物标志物提供了消费者特定饮食来源保留及其对汞生物积累影响的相关证据,而 pH 值和营养是控制湖泊之间汞生物积累差异的基础理化湖参数。