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PRESSURES
IN WATER POLLUTION
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INTRODUCTION
These are the pressures on the functionality and quality of the system or
resource, resulting from the driving forces mentioned above.STANDARD
PRESSURES
A water quality index gives an adequate overall
summary of water quality based on the pressures (indicators) derived from the driving
forces, which in turn will determine the catchment status of the water and the
related catchment impact.
The index is geared to establish the pollution status of the water,
which is based on:
- Trophic status of the water and thus the potential for algal growth
- General organic and inorganic pollution
- Sewage in the water
- Mine pollution
- Erosion
The index is extremely useful for pinpointing polluted areas, tracking
management strategies for solving pollution problems, establishing trends and seasonal
variations (Cydna Laboratories, 1998).
- A water quality index method developed by Umgeni Water has been adapted for Cydna
Laboratories (see Table ). The parameters / indicators
were selected according to the uses of surface water.
- The Jukskei Forum developed an index based on the pressures as prescribe by DWAF for
different water users.
Within Johannesburg the main uses of surface water are:
- Recreation: e.g. wind surfing, canoeing and swimming
- Environment: health of fish stock, survival of fauna and flora.
- Domestic: drinking, cooking, cleaning
- Industry : discharge of effluents
These pressures or (indicators) are being used
to determine the state and impact of the driving forces. The pressures are being
determined through sampling
points across the two catchment areas. A colour code is then assigned to the sampling
point according to the severity of the pressure.
Each driving force of water impacts on the environment whereas the pressures of these
driving forces may have a cumulative effect. The list of pressures constituted by the
driving forces follows. An increase in one of these pressures will determine the severity
of the driving force.
INDICATOR PARAMETERS FOR DETERMING THE PRESSURE AND IN TURN THE STATE
AND IMPACT OF THE CATCHMENT
Dissolved Oxygen (DO)
DO is a very important indicator of water quality. Low DO values
normally point to organic pollution. Natural water has the ability to stabilise pollutants
that enter the environment, but if the natural self-purifying ability of the water is
overpowered then the DO is depleted and anaerobic conditions set in which results in bad
smells and fish mortalities. At the opposite end of the scale too much oxygen
(supersaturation) can also cause bubble disease and mortality in fish. Supersaturation is
often caused by prolific algae growths.
pH
- pH is an indication of whether a water sample is acid, alkaline
or neutral:
- pH below 7,0 is acidic
- pH above 7,0 is alkalinic
- pH at exactly 7,0 is neutral
- Increases in pH increases the ammonia toxicity to aquatic life;
- Lowering of pH increases the cyanide toxicity;
- Acid water adversely affects tanneries, textile industries, steam generation and will
speed up corrosion of water pipes.
Electrical
conductivity
Conductivity is a convenient way of determining the total dissolved solids (TDS) of
a water sample. By applying an empirical factor of 6,6 to the conductivity, expressed in
mS/m (milli Siemens per meter), a reasonable estimate of the dissolved solids in the water
is obtained, expressed as mg/l. High TDS content may lead to:
- Scaling occurring in pipes, which results in lower water supply flows or increased
pumping costs;
- Premature replacement of geysers and household utensils;
- Sodium and Magnesium sulphate will have a laxative effect on consumers.
Turbidity
High turbidity values will shorten filter runs at water
purification plants. Silting up of an impoundment will be speeded up considerably by high
amounts of suspended solids.
Chemical
Oxygen Demand (COD)
The COD method is used to determine the pollution level in a water system. High COD
values are mainly caused by organic matter in the water, for example, a blocked sewer in
the vicinity.
Phosphorous
Phosphorous is an important nutrient, but phosphate in an
impoundment leads to algae blooms, which may cause:
- odours in drinking water by releasing 2-methyl-isoborneal into the water body;
- toxin production by the blue-green algae, Microcystis, also known as cyanogosin, which
is toxic enough to kill cattle that ingest this poison; and
- clogged filters at the water treatment plant, thereby increasing operational costs.
The single most common source of phosphate in water is from blocked
sewers that overflow into the stormwater systems.
Nitrogen
Ammonia in water is usually related to sewage being found in the
system.
- Ammonia concentrations of between 0,4 and 2,0 mg/l are lethal to most fish species.
- Nitrates may cause methaemogloinaemia (blue baby) in infants who drink liquids with a
nitrate concentration greater than ten (10 mg/l).
Chloride
This is another indicator of industrial or domestic pollution
entering the system.
Sulphate
Sulphates point to industrial pollution or slimes dam leachate
entering the system.
The oxidation of iron pyrite, present in the slimes dam, to sulphuric
acid is the cause of the high sulphate and low pH associated with slimes dam leachate. The
yellow-brown precipitate left on the floor of a stormwater channel or spruit receiving the
leachate, is caused by the iron in the leachate that is further oxidised to ferric iron,
which is insoluble and settles on the bottom.
Chlorophyll
Chlorophyll a and b is produced by algae.
Chlorophyll a is used to measure the algae concentration in water. Samples for
the determination are collected in amber glass bottles which are filled to the top. The
reason for the amber bottle is to block out sunlight. Filling the bottle shuts off the
oxygen supply to the algae.
Microbiological analysis
The presence of E.coli in water is an indication that waste
products originating from a warm blooded creature have entered the system. The most common
source of E.coli in the water is raw sewage.
REFERENCES
Cydna Laboratories 1998: Water Quality Index. Cydna: Houghton. |
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