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生物炭添加到砷污染土壤中会增加孔隙水中的砷浓度,但会减少番茄植物(Solanum lycopersicum L.)对砷的吸收。

Biochar addition to an arsenic contaminated soil increases arsenic concentrations in the pore water but reduces uptake to tomato plants (Solanum lycopersicum L.).

机构信息

Department of Environmental Sciences, Section of Genetics and Biotechnologies, Parco Area delle Scienze 11/A, University of Parma, 43100 Parma, Italy.

出版信息

Sci Total Environ. 2013 Jun 1;454-455:598-603. doi: 10.1016/j.scitotenv.2013.02.047. Epub 2013 Apr 10.

Abstract

Arsenic (As) concentrations in soil, soil pore water and plant tissues were evaluated in a pot experiment following the transplantation of tomato (Solanum lycopersicum L.) plantlets to a heavily As contaminated mine soil (~6000 mg kg(-1) pseudo-total As) receiving an orchard prune residue biochar amendment, with and without NPK fertiliser. An in-vitro test was also performed to establish if tomato seeds were able to germinate in various proportions of biochar added to nutrient solution (MS). Biochar significantly increased arsenic concentrations in pore water (500 μg L(-1)-2000 μg L(-1)) whilst root and shoot concentrations were significantly reduced compared to the control without biochar. Fruit As concentrations were very low (<3 μg kg(-1)), indicating minimal toxicity and transfer risk. Fertilisation was required to significantly increase plant biomass above the control after biochar addition whilst plants transplanted to biochar only were heavily stunted and chlorotic. Given that increasing the amount of biochar added to nutrient solution in-vitro reduced seed germination by up to 40%, a lack of balanced nutrient provision from biochar could be concluded. In summary, solubility and mobility of As were increased by biochar addition to this soil, but uptake to plant was reduced, and toxicity-transfer risk was negligible. Therefore leaching rather than food chain transfer appears the most probable immediate consequence of biochar addition to As contaminated soils.

摘要

在一项盆栽实验中,将番茄(Solanum lycopersicum L.)幼苗移植到受果园修剪物生物炭改良的重度砷污染矿区土壤(约 6000 毫克/千克总砷)中,评估了土壤、土壤孔隙水和植物组织中的砷浓度,同时还进行了一项体外测试,以确定番茄种子在添加不同比例生物炭的营养溶液(MS)中是否能够发芽。生物炭显著增加了孔隙水中的砷浓度(500μg/L-2000μg/L),而与不添加生物炭的对照相比,根和茎中的砷浓度显著降低。果实中的砷浓度非常低(<3μg/kg),表明毒性和转移风险极小。与添加生物炭后的对照相比,添加生物炭后需要施肥才能显著增加植物生物量,而仅移植到生物炭的植物严重矮化和黄化。鉴于在体外增加营养溶液中生物炭的添加量会使种子发芽率降低多达 40%,可以得出结论,生物炭缺乏平衡的养分供应。总之,生物炭的添加增加了土壤中砷的溶解度和迁移性,但植物对砷的吸收减少,毒性转移风险可以忽略不计。因此,与食物链转移相比,生物炭添加到砷污染土壤中最可能立即产生淋溶作用。

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