Glossary of Water Treatment Terms
Reverse Osmosis (R/O): A water
treatment process utilizing a membrane to remove dissolved minerals. The
process of osmosis occurs in nature, when a pure solution is separated
from a saline solution by a semi-permeable membrane. The pure solution
passes through the membrane until a pressure differential is reached
called the Osmotic Pressure. At this pressure differential, determined by
the constituents and concentrations in the saline solution, osmosis stops.
Reverse Osmosis reverses this process by applying pressure in excess of
the osmotic pressure to the saline solution, forcing water through the
membrane. As this occurs, most dissolved solids remain behind and are
carried out with the reject stream. The purified water can then be
utilized as needed.
TDS (Total Dissolved Solids): This is a
measure, usually given in PPM (Parts Per Million) or in milligrams per
liter (mg/l) that is used to specify the concentration of all minerals
dissolved in a water solution. This measurement is a principle factor in
determining the Osmotic Pressure of a solution and hence the operating
pressure necessary for a system to produce a reasonable amount of product
water.
Osmotic Pressure: This is the pressure differential
that develops as a result of a solution containing water and a particular
concentration of dissolved solids, including minerals and salts. The
osmotic pressure must be exceeded to produce purified water by means of
reverse osmosis. Tap water may have an osmotic pressure of about 10 PSI (1
Bar), while seawater may have an osmotic pressure of around 376 PSI (27
Bar) or more. To produce a suitable quantity of product water, reverse
osmosis systems typically operate at more than double the osmotic
pressure.
PPM (Parts per Million): This measurement is a means of
specifying the concentration of any constituent in a solution of water.
This is the same as mg/l or milligrams per liter.
Feed Water: This refers to the incoming water of a water
treatment system that has not yet been treated. Also called raw water or
source water.
Product Water: This is the term used to
describe the treated or purified water produced by a water treatment
system, including reverse osmosis systems and others. Also known as
Permeate.
Permeate: This is a term used to refer to the
water produced by a membrane process. The permeate is the water that
permeates or penetrates through the membrane as product
water.
Reject: The reject stream is the water that does not
pass through the membrane. Since minerals are left behind from the
departed permeate or product water, the reject stream is more concentrated
than the source or feed water. Hence it is also called the
concentrate.
Concentrate: Another term for the reject
stream.
Recovery Rate: This term refers to the percentage of
water recovered as product water from a given quantity of feed water. A
recovery rate of 40% would indicate that, of every 100 units of incoming
water, 40% would be converted to product water or recovered for use, and
60% would be rejected.
Barrier Layer: This refers to the
active layer of membrane material that actually separates the impurities
from the product stream or permeate. This barrier layer is supported by a
micro-porous support layer, usually made from polysulfone, which is cast
on a non-woven support material.
Membrane: The term membrane
generally refers, not only to the barrier layer described above that is
technically the membrane, but also to the entire engineered membrane
separation device, including the micro-porous support, the non-woven
support material, the carriers, product tube, anti-telescoping device, and
the construction of the element. The most commonly used membrane element
type is a spiral wound membrane element.
Spiral Wound Membrane
Element: The most common type of membrane element used in reverse
osmosis and other membrane separation technologies. The spiral wound
design was developed in California by U.S. Government funded research. The
design employs a number of layers of membrane material, folded over to
create envelopes. Each envelope incorporates a fine medium inside to
facilitate the flow of the permeate or product water, and a coarse medium
or mesh outside to facilitate the flow of the reject water or concentrate.
The reject or concentrate continues its flow direction straight through
the spiral wound element, entering one end and exiting the other end.
Meanwhile, the permeate or product water, after penetrating just one layer
of membrane, travels the inward spiral until it collects in the product
tube for delivery to the customer. Spiral wound elements must be housed in
pressure vessels.
Pressure Vessel: Membrane elements must be
installed in a pressure vessel to provide the means to supply feed water,
remove the reject or concentrate stream, delivery product water, and
contain the pressure at which membrane systems much operate. Pressure
vessels may contain from one to eight membrane elements, arranged end to
end in series. Responsible manufacturers normally use pressure vessels
with a burst pressure rating of four times the rated operating pressure to
prevent any safety issues from arising. This is especially important with
seawater systems, where operating pressures normally run over 800 PSI (56
Bar) and at times may exceed 1,000 PSI (69 Bar).
Rejection
Rate: This figure, typically 80% to 99.5%, indicates the percentage of
dissolved solids that will be rejected, or prevented from passing through
with the product water. The rejection rate is often specified for a
particular ion, such as the Chloride (Cl) ion. A seawater system with a
rejection rate of 99% would thus allow 1% of the dissolved solids to pass.
Hence a feed water of 35,000 PPM would result in a product TDS of about
350 PPM at that rejection rate. Various membrane materials and designs
provide for a range of rejection rates. Typically, a higher rejection rate
would require a higher pressure to produce the same amount of permeate as
would be produced by a similar membrane system with a lower rejection
rate. However, modern technology has produced "low pressure, high
rejection membranes" which provide excellent rejection at low pressures,
thus saving energy. These are available thus far for brackish water and
tap water applications.
Nano-Filtration (N/F):
Nano-Filtration is a membrane based treatment method with lower
rejection rates than R/O. Nano-Filtration is often employed as a water
softening device because it typically rejects larger molecules (such as
those that cause scaling and water hardness) very well, but smaller
molecules are usually allowed to pass. Nano-Filtration systems thus
usually operate at a lower pressure than similar reverse osmosis systems,
and reject less of the dissolved solids. This technology is frequently
employed in waste water treatment systems. Nano-Filtration systems can
often operate at higher recovery rates than R/O
systems.
Ultra-Filtration (U/F): Ultra-Filtration is another
membrane based treatment system which does not usually reject molecules
except for very large ones, but rejects virtually all particles. This
technology is often used to remove suspended solids from feed streams
before feeding the water or other fluid to the reverse osmosis or
nano-filtration membranes. This can be very effective when the suspended
solids load is unusually heavy or when oil or grease is present.
Ultra-Filtration can also be effectively employed as a means to remove
bacteria. U/F systems can usually achieve high recovery rates, as no
dissolved solids are rejected. U/F can be very effective in oil removal or
concentration.
Micro-Filtration: This is also a membrane
based fluid treatment technology, employing all the parameters of other
membrane technologies, but with a larger pore size. Operating parameters
are similar to those for U/F, but pore sizes are
larger.
Sub-Micronic Filtration: Sub-micronic filtration
technology is usually applied using more conventional filtration media,
but with very small pore sizes. Membranes are usually not used for this
technology. Rather, cartridge filters are employed.
Cartridge
Filter: Cartridge filters are a widely used and have been utilized for
water treatment for many decades. Cartridges are usually rated in microns.
40 microns is considered the largest particle visible to the human eye.
Typical prefiltration requirements for reverse osmosis systems are around
5 microns.
Bag Filter: Bag filters have applications similar
to cartridge filters. They are called bag filters because of their shape.
Typically the contaminants are caught inside the bag as the fluid flows
down from the top. Bag filters usually have these advantages over
cartridge filters: less bulk to dispose of, lower cost. Disadvantages for
most types of bags are lower efficiency in filtration and more possibility
of bypass. These disadvantages usually mean that a cartridge filter must
be used as the last step in reverse osmosis pretreatment, but bags can
often be employed, depending on system and feed water parameters, as a
means to reduce bulk of disposal and storage as well as operating costs.
Media (or Multi-Media) Filter: Also called depth
filters. A variety of media types may be employed in this type of
filtration device, depending on the objective of this part of the water
treatment system. Sand has been employed in this type of filter for many
decades. Media type filters are recommended for applications where large
quantities of suspended particles need to be removed economically. Usually
the media is permanent, so maintenance costs are very low. The device is
typically designed with graded media beds, arranged according to size. The
spaces between the particles of sand or other media determine the size of
particles that will be removed. The depth of the filter base is also a
critical design criteria. Water flows downward through a distributor,
through the graded media beds, and is collected by another set of
distributors installed in the bottom of the tank. The particles are left
behind in the media beds. Cleaning is accomplished by backwashing, or
reversing the flow. This flow lifts the media beds and dislodges the
particles trapped there. These are then washed away with the backwash
fluid and discharged. Media filters are often employed as one of the first
parts of the pretreatment system in membrane type water treatment systems.
Usually, additional filtration afterwards is also required, as the
particle size removed by media filters is not small enough to provide good
membrane protection.
Centrifugal Filter: The centrifugal
type filter is a very low maintenance device. It can usually be
effectively applied when the particles to be removed are fairly large and
relatively heavy. A feedwater sample collected in a bottle can be used to
determine whether such a device would be helpful. Shake the bottle
thoroughly, then let stand for 5 minutes. Any particles that have settled
to the bottom in that time would likely be removed effectively by a
centrifugal filter. For such applications, generally this type filter will
provide excellent service with almost no maintenance costs at
all.
Flow Meter: Most R/O systems require instrumentation to
monitor and control performance. Flow meters monitor the rate of flow of
water or other fluids, and are typically installed to indicate the rate of
flow of the permeate, reject, and feed streams. Some systems employ a
recycle stream for optimum membrane performance and higher recovery rates.
This recycle stream must be monitored to ensure proper system
operation.
Pressure Gauge: The operating pressure at various
stages of treatment must be monitored. Pressure gauges indicate these
pressures, and are usually installed before and after each filtration
device so that the pressure drop can be determined. This parameter is
generally required to determine the need for filter changes or cleanings.
Pressure readings are also required at pump discharges. Better systems
will also provide the pressure at the feed and reject points of the
pressure tubes containing the membranes. This permits immediate
determination of the pressure drop across the membranes, needed to
determine the condition of the membrane elements and whether such may need
cleaning.
TDS Monitor: This device indicates the permeate or
product water’s quality in terms of total dissolved solids. Some higher
class systems may incorporate a two channel monitor that compares the feedwater TDS with that of the product. The meter can then calculate and
read out the rejection rate. Most TDS monitor’s include user adjustable
set points that can alert the operator via an alarm or other indication of
a problem with the water quality. Some systems also include automatic
diverter valves to make sure that no water of high TDS enters the
customer’s storage tanks. Knowing the permeate TDS is also important in
gauging the condition of the membranes and other key system
components.
Pre-Treatment: Membrane type water treatment
systems require good pretreatment to ensure optimum system performance and
acceptable membrane life. The type and extent of the pretreatment depends
on the characteristics of the feed water, the recovery the membrane system
is designed for, the use of the produced water, and other factors.
Pretreatment always includes one or more types of prefiltration, and
almost always includes cartridge filters. Some systems may employ 3 or 4
types of prefiltration devices, chemical pretreatment, some form of
sterilization, and even U/F or Nano-Filtration. The chemicals used may
include antiscalants, pH adjustment, and biological growth control or
others, depending on the application and feedwater characteristics.
Sterilization may be effected by means of Ozone or U-V. Oxidizers such as
chlorine, bromine, iodine, potassium permanganate, and others are seldom
used in membrane systems because most membrane types are seriously damaged
by such oxidizers. However, some applications require such agents. In such
a case, the oxidizers usually have to be removed prior to contact with the
membranes by chemical or other means. The importance of good pretreatment
in membrane systems, and especially in R/O systems, cannot be
overstated.