农业土壤中的重金属污染,特别是镉(Cd),对土壤生物多样性构成严重威胁,水稻生产,和食品安全。土壤微生物通过调节土壤有机质的产生来提高土壤肥力,植物养分积累,和污染物转化。解决Cd毒性对土壤真菌群落组成的影响,土壤健康,水稻产量是水稻可持续生产的迫切需要。Vermicompost(VC)是一种有机肥料,可缓解Cd对土壤微生物多样性和功能的毒性作用,并可持续提高作物生产力。在本研究中,我们检查了不同剂量VC的影响(即,0、3和6吨ha-1)和Cd胁迫水平(即,0和25mgCdkg-1)对土壤生化属性的影响,土壤真菌群落组成,和香稻籽粒产量。结果表明,Cd的毒性显著降低了土壤肥力,真核微生物群落组成与水稻籽粒产量。然而,VC的添加减轻了Cd的毒性,并显着改善了土壤真菌群落;此外,它增强了子囊的相对丰度,绿藻门,Ciliophora,担子菌,Cd污染土壤中的Glomycta。此外,VC的添加增强了土壤的化学属性,包括土壤pH值,土壤有机碳(SOC),可用氮气(AN),总氮(TN),微生物生物量C和N,与Cd毒性条件下非VC处理土壤相比。同样,VC的施用显著提高了水稻籽粒产量,降低了水稻对Cd的吸收。植物中Cd吸收减少的一种可能解释是VC改良剂影响土壤的生物学特性,这最终降低了土壤Cd的生物有效性,并随后影响了水稻植株对Cd的吸收和积累。RDA分析确定,主要的真菌物种与土壤环境属性以及微生物生物量C和N的产生高度相关。然而,子囊的相对丰度水平,担子菌,和Glomomycta与土壤环境变量密切相关。因此,研究结果表明,在Cd污染土壤中使用VC可以促进水稻的可持续生产和Cd污染土壤的安全利用。
Heavy-metal contamination in agricultural soil, particularly of cadmium (Cd), poses serious threats to soil biodiversity, rice production, and food safety. Soil microbes improve soil fertility by regulating soil organic matter production, plant nutrient accumulation, and pollutant transformation. Addressing the impact of Cd toxicity on soil fungal community composition, soil health, and rice yield is urgently required for sustainable rice production. Vermicompost (VC) is an organic fertilizer that alleviates the toxic effects of Cd on soil microbial biodiversity and functionality and improves crop productivity sustainably. In the present study, we examined the effects of different doses of VC (i.e., 0, 3, and 6 tons ha-1) and levels of Cd stress (i.e., 0 and 25 mg Cd kg-1) on soil biochemical attributes, soil fungal community composition, and fragrant-rice grain yield. The results showed that the Cd toxicity significantly reduced soil fertility, eukaryotic microbial community composition and rice grain yield. However, the VC addition alleviated the Cd toxicity and significantly improved the soil fungal community; additionally, it enhanced the relative abundance of Ascomycota, Chlorophyta, Ciliophora, Basidiomycota, and Glomeromycta in Cd-contaminated soils. Moreover, the VC addition enhanced the soil\'s chemical attributes, including soil pH, soil organic carbon (SOC), available nitrogen (AN), total nitrogen (TN), and microbial biomass C and N, compared to non-VC treated soil under Cd toxicity conditions. Similarly, the VC application significantly increased rice grain yield and decreased the Cd uptake in rice. One possible explanation for the reduced Cd uptake in plants is that VC amendments influence the soil\'s biological properties, which ultimately reduces soil Cd bioavailability and subsequently influences the Cd uptake and accumulation in rice plants. RDA analysis determined that the leading fungal species were highly related to soil environmental attributes and microbial biomass C and N production. However, the relative abundance levels of Ascomycota, Basidiomycota, and Glomeromycta were strongly associated with soil environmental variables. Thus, the outcomes of this study reveal that the use of VC in Cd-contaminated soils could be useful for sustainable rice production and safe utilization of Cd-polluted soil.