The ecological toxicity and potential risks of heavy metals that coexist with nitrates in wastewater have aroused public attention. This study developed an immobilized Fe 3 O 4 @Cu/PVA mixotrophic… Click to show full abstract
The ecological toxicity and potential risks of heavy metals that coexist with nitrates in wastewater have aroused public attention. This study developed an immobilized Fe 3 O 4 @Cu/PVA mixotrophic reactor (Fe 3 O 4 @Cu/PVA-IMR) to investigate the effect of different Mn (II) concentrations (10 mg L −1 , 50 mg L −1 , and 90 mg L −1 ), Cd (II) concentrations (10 mg L −1 , 20 mg L −1 , and 30 mg L −1 ), and hydraulic retention time (HRT) (6 h, 8 h, and 10 h) on simultaneous nitrate, Cd (II), and Mn (II) removal. Using the advanced modified biomaterial Fe 3 O 4 @Cu/PVA as carrier to embed bacteria, the performance of the reactor was further improved. The surface morphology of Fe 3 O 4 @Cu/PVA was characterized by SEM as a rough surface three-dimensional skeleton structure. When the HRT was 10 h, Mn (II) and Cd (II) concentrations were 40 mg L −1 and 10 mg L −1 , respectively, indicating that the immobilized Pseudomonas sp. H117 with Fe 3 O 4 @Cu/PVA achieved the highest nitrate, Cd (II), and Mn (II) removal efficiencies of 100% (1.64 mg L −1 h −1 ), 98.90% (0.92 mg L −1 h −1 ), and 92.26% (3.58 mg L −1 h −1 ), respectively. Compared with a reactor without Fe 3 O 4 @Cu/PVA addition, the corresponding removal ratio increased by 22.63%, 7.09%, and 15.96%. Gas chromatography (GC) identified nitrogen as the main gaseous product. Moreover, high-throughput sequencing showed that Pseudomonas sp . H117 plays a primary role in the denitrification process.
               
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