外源菌剂联合柠檬酸强化龙葵修复土壤镉污染

设置对照（CK）、摩西球囊霉菌（GM）、摩西球囊霉菌+柠檬酸（GM+CA）、摩西球囊霉菌+巨大芽孢杆菌（GM+BM）和摩西球囊霉菌+巨大芽孢杆菌+柠檬酸（GM+BM+CA）这5个处理，通过测定土壤全Cd、有效Cd和植株Cd吸收量及微生物群落变化，分析了外源菌剂和柠檬酸添加对龙葵修复Cd污染效果的影响.结果表明，相对于CK处理，GM处理龙葵根、茎和叶生物量显著增加35.67%、41.35%和65.38%，GM+BM+CA处理龙葵根和茎生物量显著增加73.38%和75.38%.GM处理提高了龙葵各部位Cd含量但差异不显著，GM+BM+CA处理龙葵叶部的Cd含量显著提高79.34%.GM处理龙葵茎和叶Cd累积量显著提高47.51%和89.58%.GM+BM+CA处理龙葵叶部Cd累积量显著提高226.84%.GM+BM+CA处理显著增加了Cd由龙葵茎向叶的转运系数，增幅为52.47%.GM+BM+CA处理显著增加了叶的富集系数，增幅为120.53%.此外，联合修复对根际微生物群落结构也产生了影响，特别体现在诱导某些关键微生物类群，如变形菌门、放线菌门、球囊菌门和油壶菌门相对丰度增加2.00%~5.77%、0.76%~9.96%、2.11%~3.63%和0.54%~2.98%.RDA分析发现变形菌门和放线菌门与土壤全Cd呈显著负相关，球囊菌门和油壶菌门与土壤全Cd呈负相关.关键微生物的变化增强了龙葵吸收根际养分和抗Cd胁迫的能力，提高龙葵Cd累积能力，有效降低土壤全Cd含量.综上，摩西球囊霉菌、柠檬酸与巨大芽孢杆菌通过共接种的方式活化了土壤中的难溶态Cd，有助于龙葵富集更多的Cd，同时也与摩西球囊霉菌产生联合修复的效果.富集植物-微生物联合修复Cd污染土壤有较好的应用潜力.

Remediation of Soil Cadmium Contamination by Solanum nigrum L. Enhanced by the Combination of Exogenous Bacteria and Citric Acid

To determine how to strengthen the Cd-enriched plant Solanum nigrum L. to remediate cadmium(Cd)-contaminated soil, a pot experiment was conducted with five treatments:control treatment(CK), Glomus mosseae(GM), G. mosseae+citric acid(GM+CA), G. mosseae+Bacillus megaterium(GM+BM), and G. mosseae+B. megaterium+citric acid(GM+BM+CA). We measured soil total Cd, available Cd, plant Cd uptake, and microbial community changes and analyzed the effects of exogenous microbial agents and citric acid addition on the remediation effect of Cd contamination by S. nigrum L. The results showed that relative to that of the CK treatment, the root, stem, and leaf biomass of the GM treatment significantly increased by 35.67%, 41.35%, and 65.38%, and the root and stem biomass of the GM+BM+CA treatment significantly increased by 73.38% and 75.38%. The GM+BM+CA treatment significantly increased Cd accumulation in leaves by 226.84%. The GM+BM+CA treatment significantly increased the Cd transport factor from stem to leaves by 52.47%. The GM+BM+CA treatment significantly increased the leaf bioconcentration factor by 120.53%. In addition, the combined restoration also had an impact on the rhizosphere microbial community structure, especially in inducing the relative abundance of some key microbial groups such as Proteobacteria, Actinobacteria, Glomeromycota, and Olpidiomycota to increase by 2.00%-5.77%, 0.76%-9.96%, 2.11%-3.63%, and 0.54%-2.98%, respectively. According to the RDA analysis, Proteobacteria and Actinobacteria were negatively correlated with soil total Cd, whereas Glomeromycota and Olpidiomycota were negatively correlated with soil total Cd. The changes in key microorganisms enhanced the ability of S. nigrum L. to absorb rhizosphere nutrients and resist Cd stress, increased the Cd accumulation ability of S. nigrum L., and effectively reduced the total Cd content in soil. In conclusion, G. mosseae, citric acid, and B. megaterium activated insoluble Cd in the soil by co-inoculation, which contributed to more Cd accumulation by S. nigrum L. and also produced co-remediation with G. mosseae. The enrichment plant-microorganism combined remediation Cd-contaminated soil has good application potential.