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木材衍生生物炭与堆肥或铁砂结合用于原位稳定污染土壤中的镉、铅和锌。

Wood-derived-biochar combined with compost or iron grit for in situ stabilization of Cd, Pb, and Zn in a contaminated soil.

作者信息

Oustriere Nadège, Marchand Lilian, Rosette Gabriel, Friesl-Hanl Wolfgang, Mench Michel

机构信息

BIOGECO, INRA, University of Bordeaux, 33615, Pessac cedex, France.

Energy Department, AIT Austrian Institute of Technology GmbH, Konrad-Lorenz-Straße 24, 3430, Tulln, Austria.

出版信息

Environ Sci Pollut Res Int. 2017 Mar;24(8):7468-7481. doi: 10.1007/s11356-017-8361-6. Epub 2017 Jan 22.

Abstract

In situ stabilization of Cd, Pb, and Zn in an Austrian agricultural soil contaminated by atmospheric depositions from a smelter plant was assessed with a pine bark chip-derived biochar, alone and in combination with either compost or iron grit. Biochar amendment was also trialed in an uncontaminated soil to detect any detrimental effect. The pot experiment consisted in ten soil treatments (% w/w): untreated contaminated soil (Unt); Unt soil amended with biochar alone (1%: B1; 2.5%: B2.5) and in combination: B1 and B2.5 + 5% compost (B1C and B2.5C), B1 and B2.5 + 1% iron grit (B1Z and B2.5Z); uncontaminated soil (Ctrl); Ctrl soil amended with 1 or 2.5% biochar (CtrlB1, CtrlB2.5). After a 3-month reaction period, the soil pore water (SPW) was sampled in potted soils and dwarf beans were grown for a 2-week period. The SPW Cd, Pb, and Zn concentrations decreased in all amended-contaminated soils. The biochar effects increased with its addition rate and its combination with either compost or iron grit. Shoot Cd and Zn removals by beans were reduced and shoot Cd, Pb, and Zn concentrations decreased to common values in all amended soils except the B1 soil. Decreases in the SPW Cd/Pb/Zn concentrations did not improve the root and shoot yields of plants as compared to the Ctrl soil.

摘要

利用源自松树皮碎片的生物炭,单独或与堆肥或铁砂混合,评估了奥地利一处受冶炼厂大气沉降污染的农业土壤中镉、铅和锌的原位稳定化情况。还在未受污染的土壤中进行了生物炭改良试验,以检测是否有任何有害影响。盆栽试验包括十种土壤处理(重量百分比):未处理的污染土壤(Unt);仅用生物炭改良的Unt土壤(1%:B1;2.5%:B2.5)以及组合处理:B1和B2.5 + 5%堆肥(B1C和B2.5C),B1和B2.5 + 1%铁砂(B1Z和B2.5Z);未受污染的土壤(Ctrl);用1%或2.5%生物炭改良的Ctrl土壤(CtrlB1,CtrlB2.5)。经过3个月的反应期后,对盆栽土壤中的土壤孔隙水(SPW)进行采样,并种植矮生豆类植物两周。所有改良污染土壤中SPW的镉、铅和锌浓度均下降。生物炭的效果随着添加率以及与堆肥或铁砂的组合而增强。豆类植物地上部镉和锌的去除量减少,除B1土壤外,所有改良土壤中地上部镉、铅和锌的浓度均降至常见值。与Ctrl土壤相比,SPW中镉/铅/锌浓度的降低并未提高植物的根和地上部产量。

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