School of GeoSciences, University of Edinburgh, Edinburgh, UK.
School of GeoSciences, University of Edinburgh, Edinburgh, UK.
Environ Pollut. 2021 Jun 15;279:116909. doi: 10.1016/j.envpol.2021.116909. Epub 2021 Mar 10.
Inoculation of soil or seeds with plant growth promoting bacteria ameliorates metal toxicity to plants by changing metal speciation in plant tissues but the exact location of these changes remains unknown. Knowing where the changes occur is a critical first step to establish whether metal speciation changes are driven by microbial metabolism or by plant responses. Since bacteria concentrate in the rhizosphere, we hypothesised steep changes in metal speciation across the rhizosphere. We tested this by comparing speciation of zinc (Zn) in roots of Brassica juncea plants grown in soil contaminated with 600 mg kg of Zn with that of bulk and rhizospheric soil using synchrotron X-ray absorption spectroscopy (XAS). Seeds were either uninoculated or inoculated with Rhizobium leguminosarum bv. trifolii and Zn was supplied in the form of sulfide (ZnS nanoparticles) and sulfate (ZnSO). Consistent with previous studies, Zn toxicity, as assessed by plant growth parameters, was alleviated in B. juncea inoculated with Rhizobium leguminosarum. XAS results showed that in both ZnS and ZnSO treatments, the most significant changes in speciation occurred between the rhizosphere and the root, and involved an increase in the proportion of organic acids and thiol complexes. In ZnS treatments, Zn phytate and Zn citrate were the dominant organic acid complexes, whilst Zn histidine also appeared in roots exposed to ZnSO. Inoculation with bacteria was associated with the appearance of Zn cysteine and Zn formate in roots, suggesting that these two forms are driven by bacterial metabolism. In contrast, Zn complexation with phytate, citrate and histidine is attributed to plant responses, perhaps in the form of exudates, some with long range influence into the bulk soil, leading to shallower speciation gradients.
通过改变植物组织中金属的形态,向土壤或种子中接种植物生长促进细菌可以改善金属对植物的毒性,但这些变化的确切位置尚不清楚。了解变化发生的位置是确定金属形态变化是由微生物代谢还是由植物反应驱动的关键第一步。由于细菌集中在根际,我们假设根际的金属形态会发生急剧变化。我们通过比较用同步加速器 X 射线吸收光谱(XAS)在受 600 mg kg Zn 污染的土壤中生长的 Brassica juncea 植物根部的锌(Zn)形态与总量和根际土壤的 Zn 形态,来验证这一假设。种子要么未接种,要么接种了 Rhizobium leguminosarum bv. trifolii,Zn 以硫化物(ZnS 纳米颗粒)和硫酸盐(ZnSO)的形式供应。与先前的研究一致,接种 Rhizobium leguminosarum 的 B. juncea 减轻了 Zn 毒性,这可以通过植物生长参数来评估。XAS 结果表明,在 ZnS 和 ZnSO 处理中,形态变化最显著的是在根际和根部之间,涉及有机酸和硫醇络合物比例的增加。在 ZnS 处理中,Zn 植酸和 Zn 柠檬酸盐是主要的有机酸络合物,而 Zn 组氨酸也出现在暴露于 ZnSO 的根部中。细菌接种与根中 Zn 半胱氨酸和 Zn 甲酸盐的出现有关,这表明这两种形式是由细菌代谢驱动的。相比之下,植酸盐、柠檬酸盐和组氨酸与 Zn 的络合归因于植物反应,可能以分泌物的形式存在,其中一些具有长程影响进入总量土壤,导致形态变化梯度变浅。