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Reverse Osmosis Treatment
For Drinking Water
Other fact sheets in this series identify
reverse osmosis, commonly called RO, as a treatment process for removing
many different contaminants from drinking water. This document provides
greater detail concerning RO treatment.
WHAT IS REVERSE OSMOSIS
TREATMENT?
Many decades ago, scientists noted that
water molecules would spontaneously migrate through certain membranes that
were separating a dilute solution from a concentrated solution. This phenomenon
is called osmosis. They also noted that if pressure was added to contaminant
solution, this natural flow could be "reversed". This reversal allows the contaminant solution to be concentrated further and allows purified water to be produced.
AMOUNT OF WATER TO BE
TREATED
Where only a small volume of treated water
is needed (say 0-10 gallons per day (gpd)), RO is typically the most flexible
and cost efficient treatment process available for private home use.
Devices treating small volumes of water
are often called "under-the-sink" or "point-of-use" sized treatment devices. Treatment devices which purify all water used
in a home are commonly called "whole
house" or "point-of-entry" sized water treatment devices.
CONTAMINANTS APPROPRIATE FOR RO
TREATMENT
Certain contaminants in drinking water
do not need to be fully removed from all of the water used in the home,
but only from that water which will be consumed internally or used in food
preparation. Some of these contaminants include:
arsenic
fluoride
sodium/chloride |
beryllium
radium/uranium
pesticides and herbicides |
Other contaminants needing treatment for
all water used within a home include:
radon
iron/manganese |
hydrogen sulfide
volatile organic chemicals (VOCs) |
The above breakdown is generic and assumes
only modest levels of contaminants in the water supply. Where contaminants
are very high, whole house treatment is likely required for all contaminants.
THE RO TREATMENT DEVICE
An RO device typically consists of the
membrane housing and "pre"
and "post"
filters. The stainless steel housing containing the membrane, would
be at a minimum, approximately 3" in diameter x 10" long and the pre and
post filters would be of similar size. The
membrane would likely be of the spiral wound type. The housing would have
three connection ports to accommodate the three flows regimes of a RO device:
1. A raw water "feed-in" port;
2. A treated water "outlet" port; and
3. A reject water "outlet" port.
Operationally, an RO device functions as follows.
Raw water from the source is fed onto one side of this membrane. Some water
migrates through the membrane and accumulates in a small water storage
tank on the "treated water" side of the device. This pure water is called the permeate water.
Impurities and the remaining raw water stay on the raw water side of the
membrane. This water, called the reject water, is not further used
and is discharged from the device continuously when the device is producing
treated water. Typically this reject wastewater is discharged to
a sewer, leachfield or dry well. The reject water has a higher concentration
of contaminants than the raw water had. Disposal (wasting) of the reject
water is a major concern in arid areas.
EFFICIENCY OF THE RO PROCESS.
The efficiency of the RO process can be
measured in two ways; using both purity and volume.
1. Efficiency based on the
purity of the treated water. RO can typically remove 80-99 percent
of most mineral contaminants. For example: if the concentration of contaminants
in the raw water was 1.0 milligram per liter (mg/L) and the efficiency
of the treatment device was 90 percent for that contaminant; the treated
water contaminant concentration would be approximately 0.1 mg/L. Treated
water quality is the most important measure of the efficiency of an RO
device.
2. Efficiency based on a volume of treated
water. In New Hampshire treatment efficiency based on the volume of
water produced is poor; typically in the range of 20-30 percent. This
is due to the typically cool temperatures of the states's groundwater.
Example: Assuming the volumetric efficiency of an RO treatment device was
25 percent; if 10 gallons of raw water is fed into the device daily, only
2.5 gallons of water will migrate through the membrane to become treated
pure water. The contaminants and the remaining 7.5 gallons of water will
become reject water and will be discharged to a sewer, leachfield, or drywell.
Typical New Hampshire groundwater temperature is 40-45 degrees Fahrenheit.
This temperature is fairly constant year round. RO devices are typically
rated at an operational temperature of 77 F at 60 pounds per square inch
(psi) applied pressure. The problem causing this low rate of production
is the viscosity (stickiness) of the water when cold.
The amount of water wasted in the "under-the-sink"
size is a relatively small amount (7.5 gpd in the above example) when compared
to the total average household usage of over 200 gallons per day for a
family of four persons.
WATER QUALITY CONSTRAINTS FOR RO
DEVICES
RO treatment can be affected by some water
quality factors including:
Turbidity (cloudiness)
To accomplish separation of water from
contaminants, the passageways in the membrane must be very small. Thus
these membranes are very sensitive to clogging by small solid particles.
Where there are any particles in the raw water, a sediment prefilter must
be installed. Sediment cartridge filters are so inexpensive that it is
normally good practice to installed a prefilter before all RO units, regardless
of the solids content of the raw water.
Where waters are very clear, the pre-filter
size chosen is typically 5 microns. Where the raw water has more solids,
the 5 micron filter could be preceded by a filter of larger pore size,
approximately 25 or 50 microns.
Iron & Manganese
These naturally occurring contaminants
often create particles which will clog RO membranes. A particle filter
is critical where iron or manganese concentrations are high.
Hydrogen Sulfide
This material can create a gelatinous coating
on the membrane. This may limit the life of an RO cartridge. Where hydrogen
sulfide is high, other pretreatments may also be necessary such as oxidation.
Chlorine
Some RO membranes, called thin film composite
(TFC), will be damaged by the presence of chlorine or other strong oxidizing
compounds. Either a chlorine resistance membrane, such as cellose acetate (CA)
must be used, or the chemical injection point for the chlorine should be
placed after the RO unit.
OTHER RO APPURTENANCES
Conservation of Reject Water
To prevent the constant wasting of water
from the reject port, an automatic valve is often added to the waste discharge
line. This valve shuts off the raw water feed as the treated water pressure
tank approaches a near full capacity. This valve is available on more sophisticated
RO designs.
Differential Pressure Across The
Membrane
The greater the pressure differential pressure
across the RO membrane, the higher the purity of the treated water.
When the small accumulation pressure tank is nearly full, the differential
pressure across the RO membrane drops to near zero. This creates the potential
for excess contaminants to diffuse across the membrane and recontaminate
the purified water. To prevent this recontamination, more sophisticated
designs add two additional functions that activate when the device is not
producing water. One turns off the feed water when the accumulation tank
is near filled and the second purges the raw water side of the membrane,
with treated water. These designs features are valuable but they also raise
the cost of the RO device.
Pre and Post Activated CarbonFilters
We have already mentioned the importance
of a sediment pre-filter before the RO unit. After the RO unit, the water
conditioning industry normally advocates the installation of an activated
carbon filter. The activated carbon targets taste and odor constituents
which have escape treatment.
BACKUP AND REDUNDANCY
A very conservative design would provide
a further treatment device down stream of the RO element to address the
small concentration of contaminants that escaped through the main treatment
device, particularly in point-of-use sized treatment. Such a device would
address the possibility of rupture of the membrane or leakage of the internal
membrane cartridge. Typically a media filter is used for this backup. The
media type and associated contaminants are shown below.
Backup
Media
Activated alumina
Cartridge Ion exchange
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Target Contaminant
Arsenic, beryllium and fluoride
Uranium, radium, other ions
Sodium and chloride |
PURCHASE AND INSTALLATION
If purchasing water treatment equipment,
see the DES fact sheet WD-WSEB-2-5 entitled, "Considerations
When Purchasing Water Treatment Equipment".
The purified water accumulated in the pressure
tank. This water is typically dispensed by a special dedicated faucet mounted
on the kitchen sink. This treated water can also be plumbed directly to
the refrigerator ice maker.
The RO device can be installed in the basement
or "under-the-sink"
location. The basement location typically provides the greater ease of
maintenance. Be sure to check the adequacy of the plumbing at both the
water supply connection point and waste discharge connection point.
RO MAINTENANCE
In order to ensure proper operation, the
home owner must establish and carry out a maintenance program for any treatment
device. For RO system this program would consist of:
1. Periodic replacement of the
particle pre-filter and or post filter;
2. Periodic water quality testing of the
treated water;
3. Possible raw water testing ; and
3. Evaluation of RO membrane
integrity.
The membrane would need to be replaced at
some point. This can be estimated from the differential pressure build
up on the membrane and results of the treated versus raw water quality
tests. Your sales representative can provide an estimate of the membrane's
longevity under specific operating condition.
FOR MORE INFORMATION
For more information, please call the DES
Water Supply Engineering Bureau at call 271-3139. We would appreciate your
comments of this fact sheet. For a full list of fact sheets please request
WD-WSEB-15-2. Drinking water fact sheets are available through the
DES web site at: http://www.des.state.nh.us
then select fact sheets.
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