National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China.
Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou 510640, China.
Environ Sci Technol. 2021 Oct 5;55(19):12902-12913. doi: 10.1021/acs.est.0c04713. Epub 2021 Sep 14.
The drainage of rice soils increases Cd solubility and results in high Cd concentrations in rice grains. However, plant Cd uptake is limited by sorption to iron plaques, and Cd redistribution in the plant is regulated by the nodes. To better understand the interplay of Cd uptake and redistribution in rice under drained and flooded conditions, we determined stable Cd isotope ratios and the expression of genes coding transporters that can transport Cd into the plant cells in a pot experiment. In soil, both water management practices showed similar patterns of isotope variation: the soil solution was enriched in heavy isotopes, and the root Fe plaque was enriched in light isotopes. In rice, the leaves were heavier (ΔCd = 0.17 to 0.96‰) and the nodes were moderately lighter (ΔCd = -0.26 to 0.00‰) relative to the shoots under flooded conditions, indicating preferential retention of light isotopes in nodes and export of heavy isotopes toward leaves. This is generally reversed under drained conditions (ΔCd = -0.25 to -0.04‰, ΔCd = 0.10 to 0.19‰). The drained treatment resulted in significantly higher expression of and (phloem loading) but lower expression of (vacuolar sequestration) in nodes and flag leaves relative to the flooded treatment. It appeared that OsHMA2 and OsLCT1 might preferentially transport isotopically heavier Cd, and the excess Cd was purposefully retranslocated via the phloem under drained conditions when the vacuoles could not retain more Cd. Cd in seeds was isotopically heavier than that in stems under both water management practices, indicating that heavy isotopes were preferentially transferred toward seeds via the phloem, leaving light isotopes retained in stems. These findings demonstrate that the Fe plaque preferentially adsorbs and occludes light Cd isotopes on the root surface, and distinct water management practices alter the gene expression of key transporters in the nodes, which corresponds to a change in isotope fractionation between shoots and nodes/leaves.
排水会增加土壤中镉的溶解度,导致大米中镉含量升高。然而,植物对镉的吸收受到铁斑的吸附限制,镉在植物体内的再分配受节间的调控。为了更好地理解在排水和淹水条件下水稻对镉的吸收和再分配的相互作用,我们在盆栽实验中测定了稳定的镉同位素比值和编码可将镉运入植物细胞的转运体的基因表达。在土壤中,两种水分管理措施都表现出相似的同位素变化模式:土壤溶液中富含重同位素,而根铁斑中富含轻同位素。在淹水条件下,与地上部分相比,叶片较重(ΔCd=0.17 至 0.96‰),节间稍轻(ΔCd=-0.26 至 0.00‰),表明轻同位素优先保留在节间,重同位素向叶片输出。在排水条件下,情况通常会逆转(ΔCd=-0.25 至-0.04‰,ΔCd=0.10 至 0.19‰)。与淹水处理相比,排水处理导致节点和旗叶中 OsHMA2 和 OsLCT1(韧皮部装载)的表达显著升高,而 OsNramp5(液泡隔离)的表达显著降低。似乎 OsHMA2 和 OsLCT1 可能优先运输同位素较重的 Cd,并且当液泡不能保留更多 Cd 时,通过韧皮部将过量的 Cd 有目的地再转移。在两种水分管理措施下,种子中的 Cd 同位素比茎中的 Cd 同位素更重,表明重同位素优先通过韧皮部向种子转移,而轻同位素则留在茎中。这些发现表明,铁斑在根表面优先吸附和固定轻镉同位素,而不同的水分管理措施改变了节点中关键转运体的基因表达,这与地上部分和节点/叶片之间的同位素分馏变化相对应。