College of Resources and Environment, Fujian Agriculture and Forestry University, Fuzhou, China; Institute of Environmental Engineering, National Sun Yat-Sen University, Kaohsiung, Taiwan.
Graduate School of Biotechnology and Bioengineering, Yuan Ze University, Chung-Li City, Taoyuan, Taiwan.
J Environ Manage. 2023 Aug 1;339:117947. doi: 10.1016/j.jenvman.2023.117947. Epub 2023 Apr 17.
Cr(VI) bioreduction has become a remedial alternative for Cr(VI)-polluted site cleanup. However, lack of appropriate Cr(VI)-bioreducing bacteria limit the field application of the in situ bioremediation process. In this study, two different immobilized Cr(VI)-bioreducing bacterial consortia using novel immobilization agents have been developed for Cr(VI)-polluted groundwater remediation: (1) granular activated carbon (GAC) + silica gel + Cr(VI)-bioreducing bacterial consortia (GSIB), and (2) GAC + sodium alginate (SA) + polyvinyl alcohol (PVA) + Cr(VI)-bioreducing bacterial consortia (GSPB). Moreover, two unique substrates [carbon-based agent (CBA) and emulsified polycolloid substrate (EPS)] were developed and used as the carbon sources for Cr(VI) bioreduction enhancement. The microbial diversity, dominant Cr-bioreducing bacteria, and changes of Cr(VI)-reducing genes (nsfA, yieF, and chrR) were analyzed to assess the effectiveness of Cr(VI) bioreduction. Approximately 99% of Cr(VI) could be bioreduced in microcosms with GSIB and CBA addition after 70 days of operation, which caused increased populations of total bacteria, nsfA, yieF, and chrR from 2.9 × 10 to 2.1 × 10, 4.2 × 10 to 6.3 × 10, 4.8 × 10 to 2 × 10, and 6.9 × 10 to 3.7 × 10 gene copies/L. In microcosms with CBA and suspended bacteria addition (without bacterial immobilization), the Cr(VI) reduction efficiency dropped to 60.3%, indicating that immobilized Cr-bioreducing bacteria supplement could enhance Cr(VI) bioreduction. Supplement of GSPB led to a declined bacterial growth due to the cracking of the materials. The addition of GSIB and CBA could establish a reduced condition, which favored the growth of Cr(VI)-reducing bacteria. The Cr(VI) bioreduction efficiency could be significantly improved through adsorption and bioreduction mechanisms, and production of Cr(OH) precipitates confirmed the occurrence of Cr(VI) reduction. The main Cr-bioreducing bacteria included Trichococcus, Escherichia-Shigella, and Lactobacillus. Results suggest that the developed GSIB bioremedial system could be applied to cleanup Cr(VI)-polluted groundwater effectively.
六价铬的生物还原已成为受六价铬污染场地修复的一种替代方法。然而,缺乏合适的六价铬生物还原细菌限制了原位生物修复过程的现场应用。在这项研究中,使用两种新型固定化剂开发了两种不同的固定化六价铬生物还原细菌联合体,用于受六价铬污染的地下水修复:(1)颗粒活性炭(GAC)+硅胶+六价铬生物还原细菌联合体(GSIB),和(2)GAC+海藻酸钠(SA)+聚乙烯醇(PVA)+六价铬生物还原细菌联合体(GSPB)。此外,还开发了两种独特的基质[基于碳的试剂(CBA)和乳化胶体基质(EPS)],并将其用作增强六价铬生物还原的碳源。分析了微生物多样性、优势铬还原细菌和 Cr(VI)-还原基因(nsfA、yieF 和 chrR)的变化,以评估 Cr(VI)生物还原的效果。在微宇宙中,GSIB 和 CBA 加入后,经过 70 天的运行,约有 99%的 Cr(VI)可以被生物还原,这导致总细菌、nsfA、yieF 和 chrR 的数量从 2.9×10 增加到 2.1×10、4.2×10 增加到 6.3×10、4.8×10 增加到 2×10 和 6.9×10 增加到 3.7×10 基因拷贝/L。在加入 CBA 和悬浮细菌(没有细菌固定化)的微宇宙中,Cr(VI)的还原效率下降到 60.3%,这表明固定化铬还原细菌补充剂可以增强 Cr(VI)的生物还原。GSPB 的加入会导致材料破裂,从而导致细菌生长下降。GSIB 和 CBA 的加入可以建立一个还原条件,有利于 Cr(VI)还原菌的生长。通过吸附和生物还原机制,可以显著提高 Cr(VI)的生物还原效率,Cr(OH)沉淀的生成证实了 Cr(VI)的还原。主要的铬还原细菌包括毛球菌、大肠杆菌-志贺氏菌和乳杆菌。结果表明,开发的 GSIB 生物修复系统可以有效地应用于受六价铬污染地下水的修复。