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NAMS 2002 Workshop - ICOM 2008

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Osmotically Driven Membrane Processes – 4<br />

Tuesday July 15, 10:30 AM-11:00 AM, O’ahu/Waialua<br />

Osmotic Membrane Bioreactor and Pressure Retarded Osmotic Membrane<br />

Bioreactor for Wastewater Treatment and Water Desalination<br />

A. Achilli (Speaker), University of Nevada, Reno, Reno, Nevada, USA, aachilli@unr.edu<br />

T. Cath, Colorado School of Mines, Golden, CO, USA<br />

E. Marchand, University of Nevada, Reno, Reno, Nevada, USA<br />

A. Childress, University of Nevada, Reno, Reno, Nevada, USA<br />

More stringent regulations and the ability to produce high quality effluent make<br />

membrane bioreactors (MBRs) an attractive process for domestic and industrial<br />

wastewater treatment. In a conventional MBR, microfiltration (MF) or ultrafiltration<br />

(UF) membranes are utilized and water is commonly filtered through the<br />

membranes using pressure. Suspended solids are completely rejected and<br />

substantial removal of organic carbon and nutrients can be achieved [1]. MBRs<br />

replace two pivotal stages of conventional activated sludge systems<br />

(biotreatment and clarification) with a single, integrated process. MBR effluent<br />

may be suitable for use as irrigation water, process water, or a source of potable<br />

water. For potable reuse (e.g., indirect reuse through aquifer recharge),<br />

advanced treatment such as reverse osmosis (RO), nanofiltration (NF), or<br />

chemical oxidation is necessary after the MBR [2]. The advantages of MBRs over<br />

conventional treatment have been thoroughly reviewed and include product<br />

consistency, reduced footprint, reduced sludge production due to a high biomass<br />

concentration in the bioreactor, and complete suspended solids removal from the<br />

effluent [3].<br />

A novel MBR system that utilizes a submerged forward osmosis (FO) membrane<br />

in the bioreactor is investigated in the current study. In forward osmosis, water<br />

diffuses across a selectively permeable membrane from a solution of higher<br />

water chemical potential (lower osmotic pressure) to a solution of lower water<br />

chemical potential (higher osmotic pressure); in this application, water diffuses<br />

from the bioreactor into a controlled draw solution (DS). The FO membrane acts<br />

as a barrier to solute transport and provides high rejection of contaminants<br />

present in the wastewater stream. The diluted DS is reconcentrated using RO or<br />

distillation, and being reused in the FO process; the permeate is a high-quality<br />

product water. Thus, in most wastewater treatment applications, FO is not the<br />

ultimate process but rather a high-level pretreatment step before an ultimate<br />

reconcentration/desalination process.<br />

Compared to the MF or UF process in a conventional MBR, the FO process in<br />

the osmotic membrane bioreactor (OMBR) offers the advantages of much higher<br />

rejection (semi-permeable membrane versus microporous membrane) without

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