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Climate change effects on enchytraeid performance in metal-polluted soils explained from changes in metal bioavailability and bioaccumulation

机译:从金属生物利用度和生物累积量的变化可以解释气候变化对金属污染土壤中肠线虫性能的影响

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Climate change may alter physical, chemical and biological properties of ecosystems, affecting organisms but also the fate of chemical pollutants. This study aimed to find out how changes in climate conditions (air temperature, soil moisture content) affect the toxicity of metal-polluted soils to the soft-bodied soil organism Enchytraeus crypticus, linking enchytraeid performance with changes in soil available and body metal concentrations. Bioassays with £ crypticus were performed under different combinations of air temperature (20 and 25 ℃) and soil moisture content (50% and 30% of the soil water holding capacity, WHC) in dilution series of three metal-polluted soils (mine tailing, forest and watercourse). After 21 d exposure, enchytraeid reproduction was determined, and soil available (extracted with 0.01 M CaCl_2) and body Cd, Cu, Pb and Zn concentrations in surviving adults were determined. In general, Cd, Pb and Zn availability decreased upon incubation under the different climate scenarios. In the watercourse soil, with initially higher available metal concentrations (678 μg Cd kg~(-1), 807 μg Pb kg~(-1) and 31,020 μg Zn kg~(-1)), decreases were greatest at 50% WHC probably due to metal immobilization as carbonates. Enchytraeid reproduction was negatively affected by higher available metal concentrations, with reductions up to 98% in the watercourse soil compared to the control soil at 30% WHC. Bioaccumulation of Cd, Pb and Zn was higher when drier conditions were combined with the higher temperature of 25 ℃. Changes in metal bioavailability and bioaccumulation explained the toxicity of soil polluted by metal mine wastes to enchytraeids under changing environmental conditions.
机译:气候变化可能会改变生态系统的物理,化学和生物学特性,不仅影响生物,而且影响化学污染物的命运。这项研究旨在找出气候条件的变化(气温,土壤含水量)如何影响金属污染的土壤对土壤软生物Enchytraeus crypticus的毒性,并将其与土壤可利用量和体内金属浓度的变化联系在一起。在三种金属污染土壤的稀释系列(矿山尾矿,土壤尾矿,土壤和矿物质)中,在不同温度,温度(20和25℃)和土壤水分(土壤持水量的50%和30%,WHC)的不同组合下进行了£crypticus生物测定。森林和河道)。暴露21 d后,测定其包膜的繁殖,并测定了存活的成虫的土壤(可用0.01 M CaCl_2提取)和体内Cd,Cu,Pb和Zn的浓度。通常,在不同气候条件下孵育后,Cd,Pb和Zn的可用性降低。在河道土壤中,当初始有效金属浓度较高时(678μgCd kg〜(-1),807μgPb kg〜(-1)和31,020μgZn kg〜(-1)),在WHC 50%时下降最大。可能是由于金属固定为碳酸盐。肠线虫繁殖受到较高的有效金属浓度的不利影响,与30%WHC的对照土壤相比,河道土壤中的减少高达98%。在较干燥的条件下和较高的25℃温度下,Cd,Pb和Zn的生物累积量较高。金属生物利用度和生物蓄积性的变化解释了在变化的环境条件下,金属矿山废料污染的土壤对鞘菌的毒性。

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