TY - JOUR
T1 - Biochar and GAC intensify anaerobic phenol degradation via distinctive adsorption and conductive properties
AU - Li, Qian
AU - Gao, Xin
AU - Liu, Yaqian
AU - Wang, Gaojun
AU - Li, Yu You
AU - Sano, Daisuke
AU - Wang, Xiaochang
AU - Chen, Rong
N1 - Funding Information:
This work was supported by the National Natural Science Foundation of China (Grant Nos. 51978560 , 52070148 ), the National Key Research and Development Program of China (No. 2017YFE0127300 ), and the Shaanxi Provincial Program for Innovative Research Team (No. 2019TD-025 ).
Publisher Copyright:
© 2020 Elsevier B.V.
PY - 2021/3/5
Y1 - 2021/3/5
N2 - The roles of biochar and granular activated carbon (GAC) in the enhancement of anaerobic phenol degradation were characterized through batch tests conducted at different phenol concentrations, coupled with adsorption kinetics, microbial community, and in-situ electrochemical analysis. Both biochar and GAC (15 g/L) led to markedly shorter lag times (t0) by adsorbing dissolved phenol, and faster maximum CH4 production rate (Rmax) by triggering direct interspecies electron transfer (DIET) during a two-stage (adsorption then degradation) anaerobic phenol degradation. The high adsorption capacity of GAC helped achieve a shorter t0, but less affected Rmax of subsequent phenol degradation. Compared with GAC, which showed higher conductivity but no redox activity, biochar exhibited higher electron exchange capacity (6.57 μmol e−/g). This higher electron exchange capacity stemmed from the diverse redox-active moieties, which resulted in a more efficient DIET. Meanwhile, the formation of wire-like appendages which linked the enriched DIET partners (such as Syntrophorhabdus and Methanosaeta) on biochar probably futher enhanced the electron transfer. However, hydrogenotrophic methanogenesis was still the main pathway for syntrophic phenol degradation in the suspended sludge. The in-situ analysis also confirmed that biochar and GAC acted as geobatteries and geoconductors, respectively, and that the stimulation of DIET was persistent.
AB - The roles of biochar and granular activated carbon (GAC) in the enhancement of anaerobic phenol degradation were characterized through batch tests conducted at different phenol concentrations, coupled with adsorption kinetics, microbial community, and in-situ electrochemical analysis. Both biochar and GAC (15 g/L) led to markedly shorter lag times (t0) by adsorbing dissolved phenol, and faster maximum CH4 production rate (Rmax) by triggering direct interspecies electron transfer (DIET) during a two-stage (adsorption then degradation) anaerobic phenol degradation. The high adsorption capacity of GAC helped achieve a shorter t0, but less affected Rmax of subsequent phenol degradation. Compared with GAC, which showed higher conductivity but no redox activity, biochar exhibited higher electron exchange capacity (6.57 μmol e−/g). This higher electron exchange capacity stemmed from the diverse redox-active moieties, which resulted in a more efficient DIET. Meanwhile, the formation of wire-like appendages which linked the enriched DIET partners (such as Syntrophorhabdus and Methanosaeta) on biochar probably futher enhanced the electron transfer. However, hydrogenotrophic methanogenesis was still the main pathway for syntrophic phenol degradation in the suspended sludge. The in-situ analysis also confirmed that biochar and GAC acted as geobatteries and geoconductors, respectively, and that the stimulation of DIET was persistent.
KW - Biochar
KW - Direct interspecies electron transfer
KW - GAC
KW - Methanogenesis
KW - Phenol
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U2 - 10.1016/j.jhazmat.2020.124183
DO - 10.1016/j.jhazmat.2020.124183
M3 - Article
C2 - 33092879
AN - SCOPUS:85092785345
SN - 0304-3894
VL - 405
JO - Journal of Hazardous Materials
JF - Journal of Hazardous Materials
M1 - 124183
ER -