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Changes in dissolved organic material determine exposure of stream benthic communities to UV-B radiation and heavy metals: implications for climate change

机译:溶解有机物质的变化决定了河底栖生物群落对UV-B辐射和重金属的暴露:对气候变化的影响

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Changes in regional climate in the Rocky Mountains over the next 100 years are expected to have significant effects on biogeochemical cycles and hydrological processes. In particular, decreased discharge and lower stream depth during summer when ultraviolet radiation (UVR) is the highest combined with greater photo-oxidation of dissolved organic materials (DOM) will significantly increase exposure of benthic communities to UVR. Communities in many Rocky Mountain streams are simultaneously exposed to elevated metals from abandoned mines, the toxicity and bioavailability of which are also determined by DOM. We integrated field surveys of 19 streams (21 sites) along a gradient of metal contamination with microcosm and field experiments conducted in Colorado, USA, and New Zealand to investigate the influence of DOM on bioavailability of heavy metals and exposure of benthic communities to UVR. Spatial and seasonal variation in DOM were closely related to stream discharge and significantly influenced heavy metal uptake in benthic organisms. Qualitative and quantitative changes in DOM resulting from exposure to sunlight increased UV-B (290-320 nm) penetration and toxicity of heavy metals. Results of microcosm experiments showed that benthic communities from a metal-polluted stream were tolerant of metals, but were more sensitive to UV-B than communities from a reference stream. We speculate that the greater sensitivity of these communities to UV-B resulted from costs associated with metal tolerance. Exclusion of UVR from 12 separate Colorado streams and from outdoor stream microcosms in New Zealand increased the abundance of benthic organisms (mayflies, stoneflies, and caddisflies) by 18% and 54%, respectively. Our findings demonstrate the importance of considering changes in regional climate and UV-B exposure when assessing the effects of local anthropogenic stressors.
机译:预计未来100年落基山脉地区气候的变化将对生物地球化学循环和水文过程产生重大影响。特别是在夏季,当紫外线辐射(UVR)最高时,排放量减少,溪流深度减小,而溶解的有机物(DOM)发生更大的光氧化,将大大增加底栖生物对UVR的暴露。许多落基山溪流中的社区同时暴露于废弃矿山中升高的金属,其毒性和生物利用度也由DOM确定。我们通过缩影对19条河流(21个地点)沿金属污染的梯度进行了现场调查,并在美国科罗拉多州和新西兰进行了现场实验,以调查DOM对重金属生物利用度和底栖生物暴露于UVR的影响。 DOM的空间和季节变化与溪流排放密切相关,并显着影响底栖生物对重金属的吸收。暴露于阳光下导致的DOM的质和量变化增加了UV-B(290-320 nm)的渗透和重金属的毒性。微观实验的结果表明,来自金属污染流的底栖生物群落对金属具有耐受性,但对UV-B的敏感性高于参考流的底栖生物。我们推测这些社区对UV-B的更大敏感性是由与金属耐受性相关的成本造成的。从新西兰的12条单独的科罗拉多河和室外溪流的微观世界中排除紫外线辐射,分别使底栖生物(may,石蝇和cad)的丰富度增加了18%和54%。我们的发现表明,在评估当地人为压力源的影响时,考虑区域气候变化和UV-B暴露的重要性。

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