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森林管理对河流连续体中汞生物积累和生物放大的影响。

Effects of forest management on mercury bioaccumulation and biomagnification along the river continuum.

机构信息

Department of Biology, McMaster University, 1280 Main St. W., Hamilton, Ontario L8S 4K1, Canada.

Department of Biology, McMaster University, 1280 Main St. W., Hamilton, Ontario L8S 4K1, Canada; School of Earth, Environment and Society, McMaster University, 1280 Main St. W., Hamilton, Ontario L8S 4K1, Canada.

出版信息

Environ Pollut. 2022 Oct 1;310:119810. doi: 10.1016/j.envpol.2022.119810. Epub 2022 Aug 6.

Abstract

Forest management can alter the mobilization of mercury (Hg) into headwater streams and its conversion to methylmercury (MeHg), the form that bioaccumulates in aquatic biota and biomagnifies through food webs. As headwater streams are important sources of organic materials and nutrients to larger systems, this connectivity may also increase MeHg in downstream biota through direct or indirect effects of forestry on water quality or food web structure. In this study, we collected water, seston, food sources (biofilm, leaves, organic matter), five macroinvertebrate taxa and fish (slimy sculpin; Cottus cognata) at 6 sites representing different stream orders (1-5) within three river basins with different total disturbances from forestry (both harvesting and silviculture). Methylmercury levels were highest in water and some food sources from the basin with moderate disturbance (greater clearcutting but less silviculture). Water, leaves, stoneflies and fish increased in MeHg or total Hg along the river continuum in the least disturbed basin, and there were some dissipative effects of forest management on these spatial patterns. Trophic level (δN) was a significant predictor of MeHg (and total Hg in fish) within food webs across all 18 sites, and biomagnification slopes were significantly lower in the basin with moderate total disturbance but not different in the other two basins. The elevated MeHg in lower trophic levels but its reduced trophic transfer in the basin with moderate disturbance was likely due to greater inputs of sediments and of dissolved organic carbon that is more humic, as these factors are known to both increase transport of Hg to streams and its uptake in primary producers but to also decrease MeHg bioaccumulation in consumers. Overall, these results suggest that the type of disturbance from forestry affects MeHg bioaccumulation and trophic transfer in stream food webs and some longitudinal patterns along a river continuum.

摘要

森林管理可以改变汞(Hg)向源头溪流的迁移及其转化为甲基汞(MeHg)的过程,后者是在水生生物群和食物链中生物累积并通过食物链放大的形式。由于源头溪流是为更大系统提供有机物质和营养物质的重要来源,因此,通过林业对水质或食物网结构的直接或间接影响,这种连通性也可能增加下游生物群中的 MeHg。在这项研究中,我们在三个流域的 6 个地点收集了水、悬浮物、食物源(生物膜、叶片、有机物)、5 种大型无脊椎动物类群和鱼类(粘滑的拟鲈;Cottus cognata),这些地点代表了不同的溪流等级(1-5),并受到不同程度的林业干扰(采伐和造林都有)。在受中度干扰(更多的皆伐但较少的造林)的流域中,水和一些食物源中的 MeHg 水平最高。在受干扰最小的流域中,水、叶片、石蝇和鱼类中的 MeHg 或总汞随着河流连续体的变化而增加,并且森林管理对这些空间模式有一些耗散效应。在所有 18 个地点的食物网中,营养级(δN)是 MeHg(和鱼类中的总汞)的重要预测因子,并且在中度总干扰的流域中,生物放大斜率明显较低,但在其他两个流域中没有差异。在受中度干扰的流域中,较低营养级别的 MeHg 升高,但在该流域中其在食物链中的转移减少,这可能是由于沉积物和更多腐殖质的溶解有机碳的输入增加所致,因为这些因素既增加了 Hg 向溪流的迁移及其在初级生产者中的吸收,也减少了消费者中 MeHg 的生物累积。总的来说,这些结果表明,林业干扰的类型会影响溪流食物网中的 MeHg 生物累积和营养转移,以及沿河流连续体的一些纵向模式。

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