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庭荠生物量在土壤中的降解

Degradation of Alyssum murale biomass in soil.

作者信息

Zhang Lan, Angle J Scott, Delorme Thierry, Chaney Rufus L

机构信息

Department of Natural Resource Sciences and Landscape Architecture, University of Maryland, College Park, Maryland 20742, USA.

出版信息

Int J Phytoremediation. 2005;7(3):169-76. doi: 10.1080/16226510500214475.

Abstract

The Ni-hyperaccumulating plant Alyssum murale accumulates exceptionally high concentrations of nickel in its aboveground biomass. The reasons for hyperaccumulation remain unproven; however, it has been proposed that elemental alelopathy might be important. High-Ni leaves shed by the plant may create a "toxic zone" around the plant where germination or growth of competing plants is inhibited. The efficacy of this argument will partially depend upon the rate at which leaves degrade in soil and free metals are released, and the subsequent rate at which metals are bound to soil constituents. To test the degradation of biomass of hyperaccumulators, A. murale was grown on both high- and low-Ni soils to achieve high- (12.0 g Ni/kg) and low- (0.445 g Ni/kg) Ni biomass. Shredded leaf and stem biomass were added to a serpentine soil from Oregon that was originally used to grow high-Ni biomass and a low-Ni control soil from Maryland. Biomass Ni was readily soluble and extractable, suggesting near immediate release as biomass was added to soil Extractable nickel in soil amended with biomass declined rapidly over time due to Ni binding in soil These results suggest that Ni released from biomass of Ni hyperaccumulators may significantly affect their immediate niche only for short periods of time soon after leaf fall, but repeated application may create high Ni levels under and around hyperaccumulators.

摘要

镍超积累植物庭荠地上生物量中积累了异常高浓度的镍。超积累的原因尚未得到证实;然而,有人提出元素化感作用可能很重要。该植物脱落的高镍叶片可能会在植物周围形成一个“毒性区”,抑制竞争植物的发芽或生长。这一观点的有效性将部分取决于叶片在土壤中的降解速度以及游离金属的释放速度,以及随后金属与土壤成分结合的速度。为了测试超积累植物生物量的降解情况,将庭荠种植在高镍和低镍土壤上,以获得高镍(12.0克镍/千克)和低镍(0.445克镍/千克)生物量。将切碎的叶片和茎生物量添加到俄勒冈州的一种蛇纹岩土中,该土壤最初用于种植高镍生物量,以及来自马里兰州的低镍对照土壤。生物量中的镍易于溶解和提取,这表明在将生物量添加到土壤后,镍几乎立即释放。由于镍在土壤中的结合,随着时间的推移,用生物量改良的土壤中可提取的镍迅速下降。这些结果表明,镍超积累植物生物量释放的镍可能仅在落叶后短时间内显著影响其直接生态位,但重复施用可能会在超积累植物下方和周围形成高镍水平。

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