{UAH} Membrane bioreactor (MBR) technology in waste water treatment operations
Membrane bioreactor (MBR) technology,which combines biological-activated
sludge process and membrane filtration has became more popular, abundant,
and accepted in recent years for the treatment of many types of wastewaters,
whereas the conventional activated sludge (CAS) process cannot cope
with either composition of wastewater or fluctuations of wastewater flow rate.
MBR technology is also used in cases where demand on the quality of effluent
exceeds the capability of CAS. Although MBR capital and operational costs
exceed the costs of conventional process, it seems that the upgrade of conventional process occurs even in cases when conventional treatment works well.
It can be related with increase of water price and need for water reuse as well
as with more stringent regulations on the effluent quality. Along with better
understanding of emerging contaminants in wastewater, their biodegradability,
and with their inclusion in new regulations, MBR may become a necessary
upgrade of existing technology in order to fulfill the legal requirements in
wastewater treatment plants (WWTPs).
Anerobic treatment may be used for denitrification, depending on the effluent
nitrate and total nitrogen requirements. Anaerobic zones may be used to
achieve enhanced biological phosphorus removal in any of its possible configurations.
Membrane Classification
The membrane process is a very important separation process in water and
wastewater technology, which becomes increasingly competitive and is supeMembrane
Bioreactor (MBR) as an Advanced Wastewater Treatment Technology 41
prior to the traditional water technology with proven performance and process
economics. The most widely applied membrane separation processes are microfiltration
(MF), ultrafiltration (UF), nanofiltration (NF), reverse osmosis
(RO), electrodialysis (ED) and electro deionization (EDI),whereas the first four
processes produce permeate and concentrate.
Firstly, application of membrane-based technologies in wastewater
treatment was focused on tertiary treatment of secondary effluent, so as
to obtain a high-quality final effluent that can be reused for different purposes.
However, over the past 10 years, MBRs have emerged as an effective secondary
Treatment technology, whereas membranes applied are usually in the range of
those of MF and UF.
Membranes are usually made from different plastic and ceramic materials,
but metallic membranes also exist. The most widely used materials are celluloses,
polyamides, polysulphone, charged polysulphone and other polymeric
materials such as polyacrylonitrile (PAN), polyvinylidene difluoride (PVDF),
polyethylsulphone (PES), polyethylene (PE), and polypropylene (PP). All of
these polymeric materials have a desirable chemical and physical resistance.
All commercially available membranes are therefore modified by
chemical oxidation, organic chemical reaction, plasma treatment, or by grafting
to achieve more hydrophilic surface. This modification process usually
differs one membrane from another together with the method of fabrication
of the membrane module.
Types of Membrane Bioreactor Configurations
Membrane separation is carried out either by pressure-driven filtration in
side-stream MBRs or with vacuum-driven membranes immersed directly
into the bioreactor, which operates in dead-end mode in submerged
MBRs. The more common MBR configuration for wastewater treatment
is the latter one, with immersed membranes, although a side-stream
configuration is also possible, with wastewater pumped through the membrane
module and then returned to the bioreactor.
The energy consumption required for filtration in submerged MBR is
significantly lower . Both configurations need a shear over the membrane
surface to prevent membrane fouling with the constituents of mixed
liquor. Side-stream MBRs provide this shear through pumping, as with most
other membrane processes, whereas immersed processes employ aeration
in the bioreactor to provide it.
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