Global Centre for Environmental Remediation (GCER), College of Engineering, Science and Environment, The University of Newcastle, Callaghan, NSW 2308, Australia; Cooperative Research Centre for Contamination Assessment and Remediation of the Environment (CRC CARE), The University of Newcastle, Callaghan, NSW 2308, Australia; Department of Agriculture, Noakhali Science and Technology University (NSTU), Noakhali 3814, Bangladesh.
Global Centre for Environmental Remediation (GCER), College of Engineering, Science and Environment, The University of Newcastle, Callaghan, NSW 2308, Australia; Cooperative Research Centre for Contamination Assessment and Remediation of the Environment (CRC CARE), The University of Newcastle, Callaghan, NSW 2308, Australia.
Sci Total Environ. 2022 Mar 1;810:152296. doi: 10.1016/j.scitotenv.2021.152296. Epub 2021 Dec 9.
Cadmium (Cd) is a widespread environmental contaminant, and its increasing concentrations in rice poses significant risks to human health. Globally, rice is a staple food for millions of people, and consequently, effective strategies to reduce Cd accumulation in rice are needed. This study investigates the effect of soil pH (Soil 1: 4.6; Soil 2: 6.6) and iron (Fe) application (at 0, 1.0 and 2.0 g/kg) on Fe plaque formation, Cd sequestration in Fe plaques and Cd bioaccumulation in different parts of the rice plant for three different Cd-graded paddy soils (0, 1.0 and 3.0 mg/kg, respectively) using two Australian rice cultivars under glasshouse conditions. Results show that grain and straw yield declined as Cd toxicity increased, and the toxic effects of Cd were lower in the Quest cultivar than in the Langi cultivar. With applications of Cd at 1.0 mg/kg and 3.0 mg/kg, Cd concentrations in rice grown in Soil 1 were 1.09 mg/kg and 1.37 mg/kg, respectively, while those in rice grown in Soil 2 were 0.38 mg/kg and 0.52 mg/kg, respectively. Soil pH significantly affected the bioaccumulation of Cd in different parts of the rice plant. At both levels of Cd application, Cd concentration was highest in the root, followed by the stem, leaf, husk and grain. Cd was more concentrated in Fe plaques formed by the application of Fe than in rice plant tissues. The Quest cultivar had a higher ability to produce Fe plaques and a 1.3- and 1.4-times higher Cd concentration compared with the Langi cultivar in Soils 1 and 2, respectively.
镉 (Cd) 是一种广泛存在的环境污染物,其在水稻中的浓度不断增加,对人类健康构成了重大威胁。在全球范围内,水稻是数百万人的主食,因此,需要采取有效的策略来降低水稻中 Cd 的积累。本研究调查了土壤 pH(土壤 1:4.6;土壤 2:6.6)和铁(Fe)施用量(0、1.0 和 2.0 g/kg)对铁斑形成、Fe 斑块中 Cd 固定以及不同 Cd 分级稻田中水稻植株不同部位 Cd 生物积累的影响(分别为 0、1.0 和 3.0 mg/kg)使用两种澳大利亚水稻品种在温室条件下。结果表明,随着 Cd 毒性的增加,籽粒和稻草产量下降,Quest 品种的 Cd 毒性低于 Langi 品种。在施 Cd 1.0 mg/kg 和 3.0 mg/kg 的情况下,生长在土壤 1 中的水稻中 Cd 浓度分别为 1.09 mg/kg 和 1.37 mg/kg,而生长在土壤 2 中的水稻中 Cd 浓度分别为 0.38 mg/kg 和 0.52 mg/kg。土壤 pH 显著影响水稻植株不同部位 Cd 的生物积累。在 Cd 应用的两个水平下,Cd 浓度在根部最高,其次是茎、叶、壳和籽粒。与水稻植株组织相比,应用 Fe 形成的 Fe 斑中 Cd 浓度更高。与 Langi 品种相比,Quest 品种在土壤 1 和 2 中形成 Fe 斑的能力更高,Cd 浓度分别高出 1.3 倍和 1.4 倍。