State Key Laboratory of Urban Water Resource and Environment, School of Environment, Harbin Institute of Technology, 73 Huanghe Road, Harbin 150090, PR China.
State Key Laboratory of Urban Water Resource and Environment, School of Environment, Harbin Institute of Technology, 73 Huanghe Road, Harbin 150090, PR China.
Sci Total Environ. 2024 Nov 15;951:175499. doi: 10.1016/j.scitotenv.2024.175499. Epub 2024 Aug 14.
Arbuscular mycorrhizal fungi (AMF) have been shown to effectively mitigate the detrimental effects of heavy metal stress on their plant hosts. Nevertheless, the biological activities of AMF were concurrently compromised. Biochar (BC), as an abiotic factor, had the potential compensate for this limitation. To elucidate the synergistic effects of biotic and abiotic factors, a pot experiment was conducted to assess the impact of biochar and AMF on the growth, physiological traits, and genetic expression in rice plants subjected to Cd stress. The results demonstrated that biochar significantly increased the mycorrhizal colonization rate by 22.19 %, while the combined application of biochar and AMF led to a remarkable enhancement of rice root biomass by 42.2 %. This resulted in a shift in spatial growth patterns that preferentially promoted enhanced underground development. Biochar effectively mitigated the stomatal limitations imposed by Cd on photosynthetic processes. The decrease in IBRv2 (Integrated Biomarker Response version 2) values suggested that the antioxidant system was experiencing a state of remission. An increase of Cd content within the rice root systems was observed, ranging from 33.71 % to 48.71 %, accompanied by a reduction in Cd bioavailability and mobility curtailed its translocation to the aboveground tissues. Under conditions of low soil Cd concentration (Cd ≤ 1 mg·kg), the Cd content in rice seeds from the group subjected to the combined treatment remained below the national standard (Cd ≤ 0.2 mg·kg). Furthermore, the combined treatment modulated the uptake of Fe and Zn by rice, while simultaneously suppressing the expression of genes associated with Cd transport. Collectively, the integration of biological and abiotic factors provided a novel perspective and methodological framework for safe in-situ utilization of soils with low Cd contamination.
丛枝菌根真菌(AMF)已被证明能有效减轻重金属胁迫对其植物宿主的不利影响。然而,AMF 的生物活性同时受到了损害。生物炭(BC)作为一种非生物因素,有可能弥补这一限制。为了阐明生物和非生物因素的协同作用,进行了一项盆栽实验,以评估生物炭和 AMF 对 Cd 胁迫下水稻生长、生理特性和基因表达的影响。结果表明,生物炭显著增加了丛枝菌根的定殖率,达到 22.19%,而生物炭和 AMF 的联合应用使水稻根系生物量显著增加了 42.2%。这导致了空间生长模式的转变,优先促进了地下部分的发育。生物炭有效地减轻了 Cd 对光合作用过程造成的气孔限制。IBRv2(Integrated Biomarker Response version 2)值的降低表明抗氧化系统正在缓解。在水稻根系中观察到 Cd 含量增加,范围从 33.71%到 48.71%,同时降低了 Cd 的生物利用度和迁移性,限制了其向地上组织的转移。在土壤 Cd 浓度较低(Cd≤1mg·kg)的情况下,联合处理组的水稻种子中的 Cd 含量仍低于国家标准(Cd≤0.2mg·kg)。此外,联合处理还调节了水稻对 Fe 和 Zn 的吸收,同时抑制了与 Cd 转运相关的基因的表达。综上所述,生物和非生物因素的综合作用为安全原位利用低 Cd 污染土壤提供了新的视角和方法框架。