Risse Sören B L, Puschenreiter Markus, Tognacchini Alice
Department of Forest and Soil Sciences, Institute of Soil Research, University of Natural Resources and Life Sciences, Konrad-Lorenz-Straße 24, 3430 Tulln, Austria.
Centre for Microbiology and Environmental Systems Science, Department for Environmental Geosciences, University of Vienna, Althanstrasse 14, 1090 Vienna, Austria.
Plant Soil. 2024;495(1-2):43-56. doi: 10.1007/s11104-023-06161-w. Epub 2023 Jul 12.
Plant Ni uptake in aboveground biomass exceeding concentrations of 1000 μg g in dry weight is defined as Ni hyperaccumulation. Whether hyperaccumulators are capable of mobilizing larger Ni pools than non-accumulators is still debated and rhizosphere processes are still largely unknown. The aim of this study was to investigate rhizosphere processes and possible Ni mobilization by the Ni hyperaccumulator and to test Ni uptake in relation to a soil Ni gradient.
The Ni hyperaccumulator was grown in a pot experiment on six soils showing a pseudo-total Ni and labile (DTPA-extractable) Ni gradient and on an additional soil showing high pseudo-total but low labile Ni. Soil pore water was sampled to monitor changes in soil solution ionome, pH, and dissolved organic carbon (DOC) along the experiment.
Results showed that Ni and Fe concentrations, pH as well as DOC concentrations in pore water were significantly increased by compared to unplanted soils. A positive correlation between Ni in shoots and pseudo-total concentrations and pH in soil was observed, although plant Ni concentrations did not clearly show the same linear pattern with soil available Ni.
This study shows a clear root-induced Ni and Fe mobilization in the rhizosphere of and suggests a rhizosphere mechanism based on soil alkalinization and exudation of organic ligands. Furthermore, it was demonstrated that soil pH and pseudo-total Ni are better predictors of Ni plant uptake in than labile soil Ni.
The online version contains supplementary material available at 10.1007/s11104-023-06161-w.
植物地上生物量中镍的吸收量超过干重1000μg/g的浓度被定义为镍超积累。超积累植物是否能够比非积累植物调动更大的镍库仍存在争议,并且根际过程在很大程度上仍然未知。本研究的目的是调查镍超积累植物的根际过程和可能的镍调动情况,并测试与土壤镍梯度相关的镍吸收。
在盆栽试验中,将镍超积累植物种植在六种呈现伪总镍和不稳定(DTPA可提取)镍梯度的土壤上,以及另一种呈现高伪总镍但低不稳定镍的土壤上。在实验过程中采集土壤孔隙水,以监测土壤溶液离子组、pH值和溶解有机碳(DOC)的变化。
结果表明,与未种植的土壤相比,孔隙水中的镍和铁浓度、pH值以及DOC浓度因种植而显著增加。观察到地上部镍与土壤伪总浓度和pH值之间呈正相关,尽管植物镍浓度与土壤有效镍并未呈现相同的线性模式。
本研究表明,在镍超积累植物的根际中存在明显的根系诱导的镍和铁调动,并提出了一种基于土壤碱化和有机配体渗出的根际机制。此外,研究表明,对于镍超积累植物而言,土壤pH值和伪总镍比不稳定土壤镍更能预测植物对镍的吸收。
在线版本包含可在10.1007/s11104-023-06161-w获取的补充材料。