Abstract
1 min readThis paper evaluates a novel sorbent for the removal of potentially toxic elements, inherent cations, and hetero-chloride from hydraulic fracturing wastewater (FWW). A series of iron-biochar (Fe-BC) composites with different Fe/BC impregnation mass ratios (0.5:1, 1:1, and 2:1) were prepared by mixing forestry wood waste-derived BC powder with an aqueous FeCl<sub>3</sub> solution and subsequently pyrolyzing them at 1000 °C in a N<sub>2</sub>-purged tubular furnace. The porosity, surface morphology, crystalline structure, and interfacial chemical behavior of the Fe-BC composites were characterized, revealing that Fe chelated with CO bonds as COFe moieties on the BC surface, which were subsequently reduced to a CC bond and nanoscale zerovalent Fe (nZVI) during pyrolysis. The performance of the Fe-BC composites was evaluated for simultaneous removal of potentially toxic elements (Cu(II), Cr(VI), Zn(II), and As(V)), inherent cations (K, Na, Ca, Mg, Ba, and Sr), hetero-chloride (1,1,2-trichlorethane (1,1,2-TCA)), and total organic carbon (TOC) from high-salinity (233 g L<sup>-1</sup> total dissolved solids (TDS)) model FWW. By elucidating the removal mechanisms of different contaminants, we demonstrated that Fe-BC (1:1) had an optimal reducing/charge-transfer reactivity owing to the homogenous distribution of nZVI with the highest Fe<sup>0</sup>/Fe<sup>2+</sup> ratio. A lower Fe content in Fe-BC (0.5:1) resulted in a rapid exhaustion of Fe<sup>0</sup>, while a higher Fe content in Fe-BC (2:1) caused severe aggregation and oxidization of Fe<sup>0</sup>, contributing to its complexation/(co-)precipitation with Fe<sup>2+</sup>/Fe<sup>3+</sup>. All of the synthesized Fe-BC composites exhibited a high removal capacity for inherent cations (3.2-7.2 g g<sup>-1</sup>) in FWW through bridging with the CO bonds and cation-π interactions. Overall, this study illustrated the potential efficacy and mechanistic roles of Fe-BC composites for (pre-)treatment of high-salinity and complex FWW.
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