Temperate climate energy-positive anaerobic secondary treatment of domestic wastewater at pilot-scale.

Water Res

Department of Civil and Environmental Engineering, Stanford University, 473 Via Ortega, Stanford, CA 94305, United States; National Science Foundation Engineering Research Center for Re-Inventing the Nation's Urban Water Infrastructure (ReNUWIt), 473 Via Ortega, Stanford, CA 94305, United States; Codiga Resource Recovery Center (CR2C), 692 Pampas Ln, Stanford, CA 94305, United States.

Published: October 2021

AI Article Synopsis

  • The study presents a pilot-scale anaerobic secondary treatment system that operates with net positive energy, utilizing a two-stage process to convert wastewater into methane.
  • It employs a staged anaerobic fluidized membrane bioreactor (SAF-MBR 2.0) that combines fluidized granular activated carbon with gas-sparged membranes for efficient waste processing.
  • Energy recovery from methane production significantly exceeds energy consumption for system operations, although membrane fouling and maintenance frequency remain challenges for optimization.

Article Abstract

Conventional aerobic secondary treatment of domestic wastewater is energy intensive. Here we report net energy positive operation of a pilot-scale anaerobic secondary treatment system in a temperate climate, with low levels of volatile solids for disposal (< 0.15 mgVSS/mgCOD) and hydraulic residence times as low as 5.3 h. This was accomplished with a second-generation staged anaerobic fluidized membrane bioreactor (SAF-MBR 2.0) consisting of a first-stage anaerobic fluidized bed reactor (AFBR) followed by a second-stage gas-sparged anaerobic membrane bioreactor (AnMBR). In stage 1, fluidized granular activated carbon (GAC) particles harbor methanogenic communities that convert soluble biodegradable COD into methane; in stage 2, submerged membranes produce system effluent (permeate) and retain particulate COD that can be hydrolyzed and/or recycled back to stage 1 for conversion to methane. An energy balance on SAF-MBR 2.0 (excluding energy from anaerobic digestion of primary suspended solids) indicated net energy positive operation (+ 0.11 kWh/m), with energy recovery from produced methane (0.39 kWh electricity/m + 0.64 kWh heat/m) exceeding energy consumption due to GAC fluidization (0.07 kWh electricity/m) and gas sparging (0.20 kWh electricity/m at an optimal flux of 12.2 L/m h). Two factors dominated the operating expenses: energy requirements and recovery cleaning frequency; these factors were in turn affected by flux conditions, membrane fouling rate, and temperature. For optimization of expenses, the frequency of low-cost maintenance cleanings was adjusted to minimize recovery cleanings while maintaining optimal flux with low energy costs. An issue still to be resolved is the occurrence of ultrafine COD in membrane permeate that accounted for much of the total effluent COD.

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Source
http://dx.doi.org/10.1016/j.watres.2021.117598DOI Listing

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