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SALINITY, HARDNESS AND ALKALINITY
The mineral content of water is referred to as Total
Dissolved Solids (TDS), reported in mg/L. (Mg/L is similar to parts per
million.) Total Dissolved Solids are also commonly referred to as
salinity. This is somewhat misleading, however, as not all the
salts found in the water are table salts. The TDS measurement includes common
elements such as sodium, calcium, magnesium, chloride, sulfate, and bicarbonate
that are combined with forms of sulfur and carbon with oxygen. Thus, TDS
includes all the dissolved constituents of other minerals such as table salt
(NaCl), gypsum (CaSO4×2H20) and calcium carbonate (CaCO3).
Hardness refers to the concentrations of calcium and
magnesium ions, but is usually reported in mg/l of CaCO3. Water hardness is
linked to scale formation and the reduced cleaning efficiency of soaps.
Alkalinity, also usually reported as mg/L of CaCO3, refers
to the amount of carbonates and bicarbonates present in the water. Alkalinity
helps control the pH of water. In natural water carbonates and bicarbonates
(related to atmospheric carbon dioxide gas) are the major constituents of
alkalinity. These naturally occurring chemicals help control the pH of water
between 7.5 and 8.5. If acid is added to water the alkalinity helps neutralize
the acid without significant change in pH (Alka-seltzer effect). In natural
waters moderate alkalinity is beneficial, since it is composed of carbonates
that can combine with calcium. Calcium carbonate forms hard stable coatings
(caliche-like) inside pipes and helps control (inhibit) corrosion. However,
excessive calcium carbonate scale formation can eventually clog pipes,
particularly in water heaters and other appliances (e.g., evaporative coolers)
susceptible to scale formation. CAP water has about 2.5 times the hardness of
Tucson groundwater, but CAP alkalinity is about 10 to 20 percent lower.
Therefore, the ability of CAP water to form scale may be slightly lower than
that of Tucsons groundwater. |
Chloramine, like chlorine, is effective in controlling biofilm,
which is a slime coating in the pipe caused by bacteria. Controlling biofilms
also tends to reduce coliform concentrations and biofilm-induced corrosion of
pipes. Because chloramine is not as reactive as chlorine with organic
compounds, fewer taste and odor problems occur.
Ozonation
Ozonation is the process of feeding ozone into a water supply
for the purpose of decolorization, deodorization, disinfection and oxidation.
Ozone, a form of oxygen, is the most powerful disinfectant, but it is not
effective in controlling biological contaminants in the distribution pipes
because it does not have a long-lasting residual. Ozonation destroys bacteria
and viruses and requires a shorter time period to treat water than most other
water treatment methods. Ozone, a reactive gas, is made by subjecting oxygen to
high electrical voltages. Ozones reactive nature allows it to readily
react with and break up many organic compounds and kill bacteria and other
organisms in the water supply. On-site production of ozone is energy-intensive.
Ozone treatment is becoming more common in the United States as questions arise
about disinfection byproducts. Ozone has been widely used in Europe for 100
years.
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| Table 6-3 Comparison of
source water quality to federal standards. The figures are averages. Actual
quality may vary at different times and places. |
Membrane Filtration
Membrane filtration is a relatively recent development. Water is
forced through membranes with small pores, and anything larger than the pore
size is filtered out. Along with removing materials such as minerals, membrane
filtration also can be used for disinfection.
Four major types of membrane filtration systems are in use:
reverse osmosis (RO); nanofiltration (NF); ultrafiltration (UF); and
microfiltration (MF). The main difference between the four types is the pore
size of the membrane. This influences the amount of energy needed to force the
water through the membrane. The membranes must be cleaned periodically. The
smaller pore membranes require the most cleaning (backwashing) which is an
energy-intensive process and wastes a significant amount of water. (See the
section on desalinization below for further discussion of RO and NF.)
- RO has the smallest pore size and removes a great variety of
materials from the water, from salts to organic materials and very small
microbes. The water to be filtered must be pretreated to prevent pore clogging.
In addition, the concentrate of materials removed by the filter is highly
saline, causing loss of available water as well as disposal problems. This
process is not primarily used for disinfection, although disinfection is
achieved in the process of desalting water.
- NF has larger pores than RO and removes, pathogens, organics
and some salts. Like RO the process requires pretreatment of water with
chemicals or a sand-based system. NF has not been used commercially on a large
scale for drinking water.
- UF has larger pores than NF and is highly effective in
removing pathogens, including parasites such as giardia, but does not remove
salts. Because it has large pores, UF does not leave a saline concentrate,
although filters must be backwashed to keep the pores open. It is used
primarily in the food and pharmaceutical industries, rather than large scale
water treatment plants.
- MF has the largest pores of the membrane systems and removes
particles, but not pathogens or organics. MF may be used as a pretreatment
process for RO or NF, thus reducing some of the problems of those systems.
Several methods can be combined in the treatment process. Tucson
Water initially chose ozone plus chloramine to treat CAP water because
officials viewed this as the most effective treatment method with the least
risk to human health. The ozone performs the initial disinfection while the
chloramine provides the residual to control microbes throughout the
distribution system. Tucson Water chose not to use chlorine in the CAP water
treatment plant because of concerns about THMs. Tucson Water and some private
water companies such as Metro Water, however, use chlorine to disinfect
groundwater. THMs generally are not a concern with groundwater since little
organic matter is found in groundwater to combine with chlorine.
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