Guangdong Provincial Research Center for Environment Pollution Control and Remediation Materials, and Guangzhou Key Laboratory of Environmental Exposure and Health, School of Environment, Jinan University, Guangzhou 510632, PR China.
Guangdong Provincial Research Center for Environment Pollution Control and Remediation Materials, and Guangzhou Key Laboratory of Environmental Exposure and Health, School of Environment, Jinan University, Guangzhou 510632, PR China.
Sci Total Environ. 2016 Nov 15;571:1183-90. doi: 10.1016/j.scitotenv.2016.07.124. Epub 2016 Jul 20.
Rice (Oryza sativa L.) plants were inoculated with two species of arbuscular mycorrhizal fungi (AMF) - Rhizophagus intraradices (RI) and Funneliformis mosseae (FM) and grown for 60days to ensure strong colonization. Subsequently, a short-term hydroponic experiment was carried out to investigate the effects of AMF on cadmium (Cd) uptake kinetics, subcellular distribution and chemical forms in rice exposed to six Cd levels (0, 0.005, 0.01, 0.025, 0.05, 0.1mM) for three days. The results showed that the uptake kinetics of Cd fitted the Michaelis-Menten model well (R(2)>0.89). AMF significantly decreased the Cd concentrations both in shoots and roots in Cd solutions. Furthermore, the decrement of Cd concentrations by FM was significantly higher than RI treatment in roots. AMF reduced the Cd concentrations markedly in the cell wall fractions at high Cd substrate (≥0.025mM). The main subcellular fraction contributed to Cd detoxification was cell wall at low Cd substrate (<0.05mM), while vacuoles at high Cd substrate (≥0.05mM). Moreover, the concentrations and proportions of Cd in inorganic and water-soluble form also reduced by AMF colonization at high Cd substrate (≥0.05mM), both in shoots and roots. This suggested that AMF could convert Cd into inactive forms which were less toxic. Therefore, AMF could enhance rice resistance to Cd through altering subcellular distribution and chemical forms of Cd in rice.
水稻植株接种两种丛枝菌根真菌(AMF) - 内根结球囊霉(RI)和摩西管柄囊霉(FM),并生长 60 天以确保强烈的定植。随后,进行了一项短期水培实验,以研究 AMF 对暴露于六种 Cd 水平(0、0.005、0.01、0.025、0.05、0.1mM)三天的水稻中 Cd 吸收动力学、亚细胞分布和化学形态的影响。结果表明,Cd 的吸收动力学很好地符合米氏-门滕模型(R²>0.89)。AMF 显著降低了 Cd 溶液中水稻地上部和根部的 Cd 浓度。此外,FM 处理对根部 Cd 浓度的降低明显高于 RI 处理。在高 Cd 基质(≥0.025mM)下,AMF 显著降低细胞壁分数中的 Cd 浓度。在低 Cd 基质(<0.05mM)下,主要的亚细胞部分有助于 Cd 解毒,而在高 Cd 基质(≥0.05mM)下则是液泡。此外,在高 Cd 基质(≥0.05mM)下,AMF 定植也降低了地上部和根部 Cd 的无机和水溶性形式的浓度和比例。这表明 AMF 可以将 Cd 转化为毒性较小的非活性形式。因此,AMF 可以通过改变水稻中 Cd 的亚细胞分布和化学形态来增强水稻对 Cd 的抗性。