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==Limitations== | ==Limitations== | ||
*Efficiency has not been widely tested | *Efficiency has not been widely tested | ||
− | *Each type of unit has specific design constraints | + | *Each type of unit has specific design constraints and limitations for use |
− | and limitations for use | ||
*Can be more costly that other treatment methods | *Can be more costly that other treatment methods | ||
*Treatment may be greatly reduced if frequent maintenance is not conducted | *Treatment may be greatly reduced if frequent maintenance is not conducted | ||
− | *Subject to freezing in cold climates | + | *Subject to freezing in cold climates |
==Description== | ==Description== |
Filtration devices (inserts) allow stormwater to pass through filter media which are designed to reduce specific stormwater pollutants, but primarily solids and oils. Pollutants are captured physically or through sorption onto the filter media. Filters may either be inserts that are retrofitted into existing catch basins or manholes, or stand alone units supplied by a manufacturer.
Filtration devices, depending on the design, can treat stormwater to reduce nutrients, sediment, floatables, metals, oil, and/or organic compounds. Different filtration media are used depending on the type of pollutant to be removed. Filter media may be a screen, fabric, activated carbon, perlite, zeolite, or other materials. Often a combination of filter media can be used to target the specific pollutants of interest.
These devices differ from structural stormwater filters in two aspects. First, these devices are proprietary and are designed to fit as an insert into the hydraulic infrastructure (eg. a catch basin). Second, the media material may have unique characteristics which are different from the soil/sand media recommended for general stormwater filtration.
Filtration devices have been developed for use in locations such as underground chambers, catch basins, trench drains, and roof drains. The manufacturer specifications should indicate key design parameters such as size, allowable flow rate, allowable pollutant concentrations, and removal efficiency. A bypass should be part of the system to allow high flows to circumvent the filtration device.
Performance data are often provided by the manufacturer. Users should review this information to ensure it was provided by an independent source
The MPCA Construction General Permit allows limited use of proprietary devices or “alternative methods.” Use of the alternative device as a stand alone BMP must be approved by the MPCA prior to installation. Approval is limited to those devices that achieve approximately 80 percent removal of total suspended solids. Additionally, the MPCA requires a two-year monitoring plan to measure the actual effectiveness of the method. If a device does not meet this 80 percent total suspended solids removal requirement, then these devices could be used as pretreatment or supplemental to another stormwater practice.
When selecting or specifying a filtration device, designers should research the following questions.
a Target pollutants - actual percentage of pollutant removal varies with each device and installation