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Membrane Filtration

Membrane Filtration

In this section, we present a more in-depth discussion of membrane filtration because the technologies most commonly used for performing secondary treatment of municipal wastewater rely on microor­ganisms suspended in the wastewater to treat it. Although these technologies work well in many situations, they have several drawbacks, including the difficulty of growing the right types of microorganisms and the physical requirement of a large site.

The use of microfiltration membrane bioreactors (MBRs), a technology that has become increasingly used in the past 10 years, overcomes many of the limitations of conventional systems. These systems have the advantage of combining a suspended-growth biological reactor with solids removal via filtration. The membranes can be designed for and operated in small spaces and with high removal efficiency of contaminants such as nitrogen, phosphorus, bacteria, biochemical oxygen demand, and total suspended solids. The membrane filtration system in effect can replace the secondary clarifier and sand filters in a typical activated sludge treatment sys­tem. Membrane filtration allows a higher biomass concentration to be maintained, thereby allowing smaller bioreactors to be used.

Membrane filtration involves the flow of water-containing pollutants across a membrane. Water permeates through the membrane into a separate channel for recovery. Because of the cross-flow movement of water and the waste constituents, materials left behind do not accumulate at the membrane surface but are carried out of the system for later recovery or disposal. The water passing through the mem­brane is called the permeate, and the water with the more concentrated materials is called the concentrate or retentate.

membrane filteration

Membranes are constructed of cellulose or other polymer material, with a maxi­mum pore size set during the manufacturing process. The requirement is that the membranes prevent passage of particles the size of microorganisms, or about 1 μm (0.001 mm), so that they remain in the system. This means that MBR systems are good for removing solid material, but the removal of dissolved wastewater components must be facilitated by using additional treatment steps. Membranes can be configured in a number of ways. For MBR applications, the two configurations most often used are hollow fibers grouped in bundles or as flat plates. The hollow-fiber bundles are connected by manifolds in units that are designed for easy changing and servicing.

Designers of MBR systems require only basic information about the wastewa­ter characteristics (e.g., influent characteristics, effluent requirements, flow data) to design an MBR system. Depending on effluent requirements, certain supplementary options can be included with the MBR system. For example, chemical addition (at various places in the treatment chain, including before the primary settling tank, before the secondary settling tank [clarifier], and before the MBR or final filters) for phosphorus removal can be included in an MBR system if needed to achieve low phosphorus concentrations in the effluent.

membrane filtration water treatment

Membrane bioreactor systems historically have been used for small-scale treat­ment applications when portions of the treatment system were shut down and the wastewater was routed around (or bypassed) during maintenance periods. However, MBR systems are now often used in full-treatment applications. In these instances, it is recommended that the installation include one additional membrane tank/unit beyond what the design would nominally call for. This “N plus 1” concept is a blend between conventional activated sludge and membrane process design. It is especially important to consider both operation and maintenance requirements when selecting the number of units for MBRs. The inclusion of an extra unit gives operators flexibility and ensures that sufficient operating capacity will be avail­able. For example, bioreactor sizing is often limited by oxygen transfer, rather than the volume required to achieve the required sludge retention time, a factor that significantly affects bioreactor numbers and sizing.

Although MBR systems provide operational flexibility with respect to flow rates, as well as the ability to readily add or subtract units as conditions dictate, that flex­ibility has limits. Membranes typically require that the water surface is maintained above a minimum elevation so that the membranes remain wet during operation. Throughout limitations are dictated by the physical properties of the membrane, and the result is that peak design flows should be no more than 1.5 to 2 times the average design flow.

If peak flows exceed that limit, either additional membranes are needed simply to process the peak flow or equalization should be included in the overall design. The equalization is done by including a separate basin (external equaliza­tion) or by maintaining water in the aeration and membrane tanks at depths higher than those required and then removing that water to accommodate high flows when necessary (internal equalization).


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