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Ecofriendly Heavy Metal Stabilization: Microbial Induced Mineral Precipitation (MIMP) and Biomineralization for Heavy Metals within the Contaminated Soil by Indigenous Bacteria

机译:Ecofriendly重金属稳定:土着细菌的污染土壤中重金属的微生物诱导矿物沉淀(MIMP)和生物矿化

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摘要

Heavy metals (HMs) pollution is a serious problem, worldwide. The present study focuses on HMs removal (HMs mobility restricted within soil) by microbial induced mineral precipitation (MIMP) using indigenous isolates. Indigenous isolates were identified as Bacillus subtilis C(225)(MK334652), Oceanobacillus indicireducens 5(225)(MK334653), and Bacillus pumilus 7(225)(MK334654) by 16S-rRNA from HMs polluted industrial-soil (soil-225) that is used for bioremediation. The studied soil contained high level (mg/kg) of Cr(307.41 +/- 1.02), Cu(576.35 +/- 1.02), and Zn(708.81 +/- 1.50) as per Taiwan permissible limit (TPL) and/or Canadian Soil Quality Guidelines (CSQG). Minimum inhibitory concentration (MIC) of Bacillus species were higher compare to Oceanobacillus. Bioavailable-fraction (F-1) of HMs (Cr/Cu/Zn) in untreated 225-soil was noticed to be higher compared to F-2-F-5 fraction. Bacillus subtilis C(225) are more efficient for HMs-mineralization, compared to other isolates where Cr/Cu/Zn immobilized within soil, transforming from bioavailable-fraction (F-1) (high-mobility) (60-90% reduction) to residual-fraction F-5 (low-mobility) (50-80% increment). Organic-bound-fraction (F-4) (medium-mobility) of Cr increased (42.66 +/- 2.1%), compared to Cu/Zn, by Bacillus subtilis C(225). Urease (40.8%) and dehydrogenase (8.3%) activity increased in bio-remediated soil, compared to control. MIMP of HMs by ingenious bacteria reflects the transformation-pathway from F-1 to F-5 of HMs to fix strongly within soils with inadequate mobility. Thus, MIMP by indigenous microbe can be applicable for HMs stabilization/removal in contaminated soil for ecofriendly environmental cleanup.
机译:重金属(HMS)污染是全世界严重的问题。本研究侧重于使用本土分离株通过微生物诱导的矿物沉淀(MIMP)的HMS去除(在土中受到限制的HMS流动性)。本土分离株被鉴定为枯草芽孢杆菌C(225)(MK334652),OceancaCillus indieduceCens 5(225)(MK334653),杆菌7(225)(MK334654)从HMS污染工业 - 土壤(土壤-225)(土壤-225)(土壤-225)达到16S-RNA用于生物修复。所研究的土壤包含高水平(Mg / kg)Cr(307.41 +/- 1.02),Cu(576.35 +/- 1.02),Zn(708.81 +/- 1.50),Zn(708.81 +/- 1.50),允许的允许极限(TPL)和/或加拿大土壤质量指南(CSQG)。芽孢杆菌物种的最小抑制浓度(MIC)与Oceanobacillus相比较高。与F-2-F-5级分相比,未处理225土壤中HMS(Cr / Cu / Zn)的生物可利用率 - 馏分(F-1)被注意到更高。与其他分离物相比,甲硝酸枯草芽孢杆菌C(225)对HMS-矿物质更有效,其中Cr / Cu / Zn固定在土壤中,从生物可利用 - 级分(F-1)(高迁移率)转化(减少60-90%)残余部分F-5(低迁移率)(增量50-80%)。与Cu / Zn的Cr增加(42.66 +/- 2.1%)的有机束 - 级分(F-4)(中等迁移率),通过枯草芽孢杆菌C(225)。与对照相比,生物修复土壤中脲酶(40.8%)和脱氢酶(8.3%)活性增加。通过巧妙的细菌MIMP的HMS反映了来自F-1至F-5的转化途径,以在具有不足的迁移率内强烈地固定在土壤中。因此,本土微生物的MIMP可适用于为Ecofriendly环境清理的受污染的土壤中的HMS稳定/去除。

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