4.8 Article

Biochar sorbents for sulfamethoxazole removal from surface water, stormwater, and wastewater effluent

Journal

WATER RESEARCH
Volume 96, Issue -, Pages 236-245

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.watres.2016.03.049

Keywords

Powdered activated carbon; Trace organic contaminants; Sorption kinetics; Dissolved organic matter; Fouling; Fluorescence

Funding

  1. Malcolm Pirnie Inc.
  2. U.S. EPA-STAR Fellowship [FP 91767301]
  3. NSF-REU [1263385]
  4. Bill and Melinda Gates Foundation
  5. Div Of Engineering Education and Centers
  6. Directorate For Engineering [1263385] Funding Source: National Science Foundation

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This study examined sorption of the human and veterinary antibiotic sulfamethoxazole (SMX) at environmentally relevant concentrations from laboratory clean water, surface water, stormwater, and wastewater effluent to wood and wastewater-sludge derived biochars produced under a wide range of conditions. SMX sorption by commercial powdered activated carbon (PAC) was also quantified as a benchmark. Wood-based biochar produced around 850 degrees C performed similarly to PAC. Biochar sorption capacity increased with surface area up to similar to 400 m(2)/g. However, a further increase in surface area did not correspond to an increase in sorption capacity. Sorbent H:C ratios correlated with SMX uptake by PAC and wood-based biochars, but not for the sludge-based biochars. This is possibly due to an indirect influence of the high ash content in sludge-based biochars, as the isolated ash fraction exhibited negligible SMX sorption capacity. The presence of dissolved organic matter (DOM) in the natural and anthropogenic waters fouled most of the sorbents (i.e., decreased SMX uptake). The sludge-based biochars experienced less DOM fouling relative to wood-based biochar, particularly in the wastewater effluent. Biochar and PAC sorption kinetics were similar when examined over a contact time of four-hours, suggesting their performance ranking would be consistent at contact times typically utilized in water treatment systems. In the presence of DOM, SMX relative removal (C/C-0) was independent of SMX initial concentration when the initial concentration was below 10 mu g/L, thus permitting the relative removal results to be applied for different SMX initial concentrations typical of environmental and anthropogenically impacted waters. (C) 2016 Elsevier Ltd. All rights reserved.

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