Chromium (Cr) is a major heavy metal pollutant that has been found in many groundwater-polluted sites. The effectiveness of hexavalent chromium [Cr(VI)] plume containment and remediation via the bioreduction and adsorption mechanisms were evaluated in this study using the developed green slow-releasing denaturing-colloidal substrates (G-SDS). The major components of G-SDS were gelatin, agar, and cane molasses (optional), and weight ratios for gelatin and agar were 3 and 0.5%, respectively. Gelatin was used for slow carbon release and Cr(VI) adsorption, cane molasses was applied for rapid carbon release, and agar was used as the solidifying agent to form G-SDS. Environmental scanning electron microscope analyses indicate that the G-SDS had a rigid and stable 3-D structure with irregular and rippled surface and staged sheets, which created significant surface areas for Cr(VI) adsorption. Results from the column study show that more than 98% of Cr(VI) was removed with increased Cr(III) concentrations in column effluents. The G-SDS could form a permeable and reticulated fiber biobarrier after its injection for Cr(VI) adsorption. The released carbon substrate from G-SDS could subsequently enhance Cr(VI) bioreduction mechanisms. The released amine from gelatin could react with water and produce ammonia, which could neutralize the acidified water due to the produced organic acids from G-SDS fermentation. The microbial communities in column soils were characterized by the next-generation sequencing technology. G-SDS supplement caused the variations in microbial diversities and predominant bacteria. The released carbon from G-SDS resulted in the formation of anaerobic conditions , and thus, the growth of the Cr(VI) reducer was enhanced. G-SDS could serve as a source of primary substrate for Cr(VI) bioreduction. The dominant groups of bacterial communities include Acinetobacter, Bacillus sp., Clostridium , Desulfovibrio, and Geobacter . Both G-SDS and column soils contained significant amounts of Cr(III) after the column experiment indicating that the adsorbed Cr(VI) within G-SDS was bioreduced to Cr(III). Moreover, Cr(OH) 3 was formed and precipitated in soils after Cr(VI) bioreduction. Results indicate that the passive biobarrier system containing G-SDS can be used as an economically and practically acceptable remedial system to contain the Cr(VI) plume and reduce the environmental risks caused by Cr(VI). G-SDS can enhance Cr(VI) removal via the development of bioreduction, adsorption, and precipitation mechanisms. • The developed G-SDS can remove Cr(VI) via the bioreduction and adsorption. • G-SDS forms semi-solidified colloid for slow and long-term carbon release. • Cr(OH) 3 is formed and precipitated after Cr(VI) bioreduction. • Dominant CRB include Acinetobacter, Bacillus , Clostridium, Desulfovibrio and Geobacter. • Released amine from G-SDS can produce ammonia, which has the buffering capacity.
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