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The Combined and Interactive Effects of Zinc, Temperature, and Phosphorus on the Structure and Functioning of a Freshwater Community

机译:锌,温度和磷对淡水群落结构和功能的联合交互作用

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Ecotoxicological studies mainly consist of single-species experiments evaluating the effects of a single stressor. However, under natural conditions aquatic communities are exposed to a mixture of stressors. The present study aimed to identify how the toxicity of zinc (Zn) is affected by increased temperature and increased phosphorus (P) supply and how these interactions vary among species, functional groups, and community structure and function. Aquatic microcosms were subjected to 3 Zn concentrations (background, no Zn added, and 75 and 300g Zn/L), 2 temperatures (16-19 and 21-24 degrees C), and 2 different P additions (low, 0.02, and high, 0.4mgP L(-1)wk(-1)) for 5 wk using a full factorial design. During the study, consistent interactions between Zn and temperature were only rarely found at the species level (4%), but were frequently found at the functional group level (36%), for community structure (100%) and for community function (100%; such as dissolved organic carbon concentrations and total chlorophyll). The majority of the Znxtemperature interactions were observed at 300g Zn/L and generally indicated a smaller effect of Zn at higher temperature. Furthermore, no clear indication was found that high P addition by itself significantly affected the overall effects of Zn on the community at any level of organization. Interestingly, though, 90% of all the Znxtemperature interactions observed at the species, group, and community composition level were found under high P addition. Collectively, the results of our study with the model chemical Zn suggest that temperature and phosphorus loading to freshwater systems should be accounted for in risk assessment, because these factors may modify the effects of chemicals on the structure and functioning of aquatic communities, especially at higher levels of biological organization. Environ Toxicol Chem 2018;37:2413-2427. (c) 2018 SETAC
机译:生态毒理学研究主要包括评估单一胁迫因素影响的单一物种实验。然而,在自然条件下,水生生物群落暴露于多种应激源下。本研究旨在确定温度升高和磷(P)供应增加如何影响锌(Zn)的毒性,以及这些相互作用在物种,功能组以及群落结构和功能之间如何变化。对水生微观世界进行3种Zn浓度(背景,未添加Zn以及75和300g Zn / L),2种温度(16-19和21-24摄氏度)和2种不同的P添加量(低,0.02和高) ,使用全阶乘设计,每5周0.4mgP L(-1)wk(-1))。在研究过程中,仅在物种水平(4%)上很少发现锌与温度之间的一致相互作用,但在功能组水平(36%),群落结构(100%)和群落功能(100上)经常见到%;例如溶解的有机碳浓度和总叶绿素)。在300g Zn / L下观察到大多数Znx温度相互作用,通常表明在较高温度下Zn的作用较小。此外,没有明确的迹象表明,高磷的添加本身会严重影响锌在任何组织水平上对社区的总体影响。有趣的是,在高磷添加条件下,在物种,群体和群落组成水平上观察到的所有Znx温度相互作用中有90%被发现。总的来说,我们对化学锌模型的研究结果表明,在风险评估中应考虑淡水系统的温度和磷负荷,因为这些因素可能会改变化学物质对水生群落结构和功能的影响,尤其是在较高的温度下。生物组织的水平。 Environ Toxicol Chem 2018; 37:2413-2427。 (c)2018年SETAC

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