Water Supply Restoration Program
Filter Systems
Point of entry (POE)
filters are installed when there are potential health risks associated with dermal contact
(washing hands) or inhalation (taking a shower). Examples of these substances include
pesticides, petroleum compounds, and solvents. Granular Activated Carbon
(GAC) filters are
the most commonly used POE filter systems installed on wells contaminated with these
substances.
Point of Use (POU) filters are installed
when the only potential health risks are associated with drinking the water (generally,
inorganic substances such as nitrate or lead). The WSRP generally uses reverse osmosis
systems installed under the kitchen sink for these contaminants.
Granular Activated Carbon
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GAC filters have been installed and maintained by the State
of Florida since January 1984, and were originally only for wells contaminated with EDB.
Since that time additional contaminants such as solvents, other pesticides and petroleum
products have been added to the list of substances filtered by GAC. We currently maintain
approximately 1,185 of these system, about 80 percent of which are operating on EDB
contaminated wells. There are approximately 150 filters currently operating on wells
contaminated with solvents and approximately 110 filters on wells with petroleum
contaminants.
Performance data for carbon filters indicates that these
filters perform extremely well for most groundwater contaminants. The configuration of
each installation is determined by the removal efficiency for that particular contaminant
and the expected peak demand. For designing, installing, and maintaining the system,
contaminants are classified as EDB (and DBCP), other pesticides and solvents, and
petroleum.
Because carbon is so effective at removing EDB, the most
common filter system used for this contaminant consists of a five micron pre-filter, a
flow meter, a single 54-inch tall by 10-inch diameter GAC tank, and an ultra-violet light
for disinfection. This system has a capacity of 6 gallons per minute (gpm) and is
sufficient for the average home. Where the demand is somewhat higher, a single 52-inch
high by 12-inch diameter tank is used which has a capacity of 10 gpm. For even higher flow
requirements, multiple tanks are installed in parallel to match the demand. For very high
levels of EDB, a second tank, or polishing tank, is added to ensure that the EDB is
effectively removed. The filter media for all systems installed for EDB is exchanged
annually.
Systems installed on wells contaminated with other
pesticides or solvents are similar to the EDB systems. However, because we have collected
less data for these systems, they all include a polishing tank. Selected filter systems,
which were installed on wells with very high concentrations of solvents or petroleum
products, were sampled quarterly to obtain performance data on removal efficiency. These
sampling results indicated that the GAC filters were so successful in removing the
contaminants that the filters are now exchanged annually, except where the contaminant is
Vinyl Chloride (VC) or Methyl-Tert-Butyl-Ether (MTBE). Filters on wells with VC are
exchanged every six months and filters on wells with MTBE continue to be sampled quarterly
and exchanged after a breakthrough at the mid-point. [Samples are obtained at a raw water
port, a port between each lead tank and polishing tank (called the mid-port), and at the
finish water port. These samples are analyzed at the DOH chemical laboratory in
Jacksonville.]
Reverse
Osmosis
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While testing in areas with EDB and other pesticide
contamination, nitrate levels greater than the State's standard of 10 mg/L were often
discovered. In 1992 the Department began to restore or replace these nitrate-contaminated
wells. In cases where a connection to public water system is not cost-effective, POU
reverse osmosis (RO) filters are installed, usually under the kitchen sink. These filters
have a total dissolved solids (TDS) indicator light to show when the filter is no longer
working properly. Over 400 of these filters have been installed to date, of which,
approximately 315 are still in operation. All RO filters are exchanged annually.
Ion
Exchange
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Where the MCL for nitrate is exceeded at a non-community
water system as defined in Rule 62-550, Florida Administrative Code, and the WSRP's
assistance is requested, a POE nitrate filter must be installed. For these systems an ion
exchange filter, containing a nitrate removal resin, is installed which is similar in
appearance to the carbon filters, although the process is quite different. These filters
are sampled quarterly, because they need to be regenerated with a brine solution, to
ensure the resin is performing satisfactorily.