College of Biological Science & Engineering, North Minzu University, Yinchuan, 750021, China.
Key Laboratory of Ecological Protection of Agro-Pastoral Ecotones in the Yellow River Basin, National Ethnic Affairs Commission of the People's Republic of China, Yinchuan, 750021, China.
Biodegradation. 2023 Oct;34(5):445-459. doi: 10.1007/s10532-023-10026-5. Epub 2023 Apr 12.
Six cadmium (Cd)-resistant microbial strains were isolated and their ability to immobilise Cd in soil investigated. Cd-1, Cd-2, Cd-5, and Cd-6 were identified as Stenotrophomonas sp., Cd-3 as Achromobacter sp., and Cd-7 as Staphylococcus sp. The six strains showed a wide adaptation range for salinity and a strong tolerance to Cd. The effects of the initial Cd concentration (1-100 mg/L), duration (18-72 h), temperature (10-40 °C), and pH (5.0-9.0) on the efficiency of Cd removal were analysed. The results revealed that the Cd removal rate was higher at an initial Cd concentration of 5-100 mg/L than at 1 mg/L. The maximum Cd removal effect was at a culture duration of 36 h, temperature of 10-35 °C, and pH of 5.0-7.0. X-ray diffraction (XRD) analysis revealed that the Cd was immobilised by Stenotrophomonas sp. Cd-2 and Staphylococcus sp. Cd-7 through bio-precipitation. X-ray photoelectron spectroscopy (XPS) revealed that the Cd was adsorbed by Stenotrophomonas sp. Cd-2, Achromobacter sp. Cd-3, and Staphylococcus sp. Cd-7. Fourier transform infrared spectroscopy (FTIR) analysis revealed that the isolates reacted with the Cd mainly through the O-H, protein N-H, C-N, lipid C-H, fatty acid COO, polysaccharide C-O, P-O, and other functional groups, as well as with lipid molecules on the cell wall surfaces. Scanning electron microscopy (SEM) analysis revealed that there was little difference in the cells after Cd treatment. The results of the soil remediation experiments indicated that the toxicity of Cd in soil could be effectively reduced using certain strains of microbe.
从土壤中分离得到 6 株镉抗性微生物菌株,并研究了它们固定土壤中镉的能力。Cd-1、Cd-2、Cd-5 和 Cd-6 被鉴定为 Stenotrophomonas sp.,Cd-3 为不动杆菌属(Achromobacter sp.),Cd-7 为葡萄球菌属(Staphylococcus sp.)。这 6 株菌对盐度具有较宽的适应范围,并且对 Cd 具有很强的耐受性。分析了初始 Cd 浓度(1-100mg/L)、时间(18-72h)、温度(10-40°C)和 pH(5.0-9.0)对 Cd 去除效率的影响。结果表明,初始 Cd 浓度为 5-100mg/L 时,Cd 的去除率高于 1mg/L。在培养时间为 36h、温度为 10-35°C、pH 为 5.0-7.0 时,Cd 的去除效果最佳。X 射线衍射(XRD)分析表明,Cd 被 Stenotrophomonas sp. Cd-2 和葡萄球菌属(Staphylococcus sp.)Cd-7 通过生物沉淀固定。X 射线光电子能谱(XPS)表明,Cd 被 Stenotrophomonas sp. Cd-2、不动杆菌属(Achromobacter sp.)Cd-3 和葡萄球菌属(Staphylococcus sp.)Cd-7 吸附。傅里叶变换红外光谱(FTIR)分析表明,分离物主要通过 O-H、蛋白质 N-H、C-N、脂类 C-H、脂肪酸 COO、多糖 C-O、P-O 等功能基团以及细胞壁表面的脂类分子与 Cd 发生反应。扫描电子显微镜(SEM)分析表明,Cd 处理后细胞差异不大。土壤修复实验结果表明,某些微生物菌株可以有效降低土壤中 Cd 的毒性。