Biotic/abiotic transformation mechanisms of phenanthrene in iron-rich constructed wetland under redox fluctuation

•Iron-rich tidal flow CW achieved the highest PHE removal and toxicity reduction.•Surface-bound/low-crystalline iron regulated ·OH production predominantly in CW.•Efficient utilization of active iron optimized both abiotic and biotic pathway in CW.•Abiotic and biotic mechanisms contributed similarly...

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Veröffentlicht in:Water research (Oxford) 2024-09, Vol.261, p.122033, Article 122033
Hauptverfasser: Lu, Jiaxing, Yu, Peihan, Zhang, Jian, Guo, Zizhang, Li, Yanwei, Wang, Shuo, Hu, Zhen
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Sprache:eng
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Zusammenfassung:•Iron-rich tidal flow CW achieved the highest PHE removal and toxicity reduction.•Surface-bound/low-crystalline iron regulated ·OH production predominantly in CW.•Efficient utilization of active iron optimized both abiotic and biotic pathway in CW.•Abiotic and biotic mechanisms contributed similarly to the transformation of PHE. Iron-rich constructed wetlands (CWs) could promote phenanthrene bioremediation efficiently through biotic and abiotic pathways, which have gained increasing attention. However, the biotic/abiotic transformation mechanisms of trace organic contaminants in iron-rich CW are still ambiguous. Herein, three CWs (i.e., CW-A: Control; CW-B: Iron-rich CW, CW-C: Iron-rich CW + tidal flow) were constructed to investigate the transformation mechanisms of phenanthrene through Mössbauer spectroscopy and metagenomics. Results demonstrated CW-C achieved the highest phenanthrene removal (94.0 %) and bacterial toxicity reduction (92.1 %) due to the optimized degradation pathway, and subsequently achieved the safe transformation of phenanthrene. Surface-bound/low-crystalline iron regulated hydroxyl radical (·OH) production predominantly, and its utilization was promoted in CW-C, which also improved electron transfer capacity. The enhanced electron transfer capacity led to the enrichment of PAH-degrading microorganisms (e.g., Thauera) and keystone species (Sphingobacteriales bacterium 46–32) in CW-C. Additionally, the abundances of phenanthrene transformation (e.g., EC:1.14.12.-) and tricarboxylic-acid-cycle (e.g., EC:2.3.3.1) enzyme were up-regulated in CW-C. Further analysis indicated that the safe transformation of phenanthrene was mainly attributed to the combined effect of abiotic (·OH and surface-bound/low-crystalline iron) and biotic (microbial community and diversity) mechanisms in CW-C, which contributed similarly. Our study revealed the essential role of active iron in the safe transformation of phenanthrene, and was beneficial for enhanced performance of iron-rich CW. [Display omitted]
ISSN:0043-1354
1879-2448
1879-2448
DOI:10.1016/j.watres.2024.122033