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WATER
DR. RAHUL.K.R
In 1981, the 34th World Health Assembly in a
resolution emphasized that safe drinking water is a
basic element of "primary health care" which is
the key to the attainment of "Health for All by the
year 2000 AD".
Water is integrated with other PHC components
because it is an essential part of health
education, food and nutrition, and also MCH
Safe and wholesome water
 This has been defined as water that is
a) free from pathogenic agents
b) free from harmful chemical substances
c) pleasant to the taste, i.e., free from colour and
odour;
d) usable for domestic purposes.
Water is said to be polluted or contaminated when it
does not fulfil the above criteria.
Water requirement
Physiological requirements for drinking water
have been estimated at about 2 litres per head
per day (just for survival).
A daily supply of 150-200 litres per capita is
considered as an adequate supply to meet the
needs for all urban domestic purposes.
In India 40 litres of water supply per capita per
day was the set target.
Uses of water
(1) Domestic use : on domestic front, water is
required for drinking, cooking, washing and
bathing, flushing of toilets, gardening etc.
(2) Public purposes : cleaning streets, recreational
purposes like swimming pools, public fountains
and ornamental ponds, fire protection and public
parks.
(3) Industrial purposes : for processing and
cooling;
Uses of water
(4) Agricultural purpose : irrigation
(5) Power production from hydropower and
steam power;
(6) Carrying away waste from all manner of
establishments and institutions.
Sources of water supply
In general, water sources must conform to two
criteria :
(a)the quantity must be sufficient to meet
present and future requirement
(b)the quality of water must be acceptable.
There are three main sources of water
Sources of water supply
1. RAIN
2. SURFACE WATER
3. GROUND WATER
Impounding reservoirs
Rivers and streams
Tanks, ponds and lakes
Shallow wells
Deep wells
Springs
Rain
Rain is the prime source of all water.
CHARACTERISTICS : Rain water is the purest
water in nature.
Physically, it . is clear, bright and sparkling.
Chemically, it is very soft water containing only
traces of dissolved solids and free from
pathogenic agents.
Rain
IMPURITIES : Rain water tends to become impure
as it passes through. the atmosphere. It picks up
suspended impurities from the atmosphere· such
as dust, soot and microorganisms and gases
such as carbon dioxide, nitrogen, oxygen and
ammonia.
Surface water
Surface water originates from rain water. It is
the main source of water supply in many
areas.
Surface water is prone to contamination from
human and animal sources. As such it is never
safe for human consumption unless subjected
to sanitary protection and purification before
use.
surface water sources
(1) Impounding Reservoirs.
(2) Rivers and Streams,
(3) Tanks, Ponds and Lakes.
In general, surface water supplies possess a high
probability of organic, bacterial and viral
contamination.
IMPOUNDING RESERVOIRS
These are artificial lakes constructed usually of
earthwork or masonry in which large quantities of
surface water is stored.
Dams built across rivers and mountain streams also
provide large reserves of surface water. The area
draining into the reservoir is called "Catchment area".
One disadvantage of storing water for long periods in
reservoirs is the growth of algae and other microscopic
organisms, which impart bad tastes and odours to
water.
IMPOUNDING RESERVOIRS
CHARACTERISTICS : Impounding reservoirs usually
furnish a fairly good quality of water. Water is
usually clear, palatable and ranks next to rain
water. The water is usually soft and considered
to be free of pathogenic organisms.
IMPURITIES : The upland surface water derives its
impurities from the catchment area, the sources
being human habitations and animal keeping or
grazing.
RIVERS
Many rivers furnish a dependable supply of water.
The chief drawback of river water is that it is
always grossly polluted and is quite unfit for
drinking without treatment.
CHARACTERISTICS : River water is turbid during
rainy season; it may be clear in other seasons. The
bacterial count, including the human intestinal
organisms may be very high.
RIVERS
IMPURITIES : Rivers are described as a direct
connection between the alimentary canal of the
people living upstream and the mouths of those
below.
Impurities of river water are derived from surface
washings, sewage and sullage water, industrial
and trade wastes, and drainage from agricultural
areas.
RIVERS
SELF-PURIFICATION : Certain amount of self-
purification does occur in river water by natural
forces of purification such as dilution,
sedimentation, aeration, oxidation, sunlight, plant
and animal life but these agencies are not
sufficient to render the water potable.
River water needs purification before it can be
used for drinking purposes.
TANKS
Tanks are large excavations in which surface
water is stored. They are an important source of
water supply in some Indian villages.
Tanks are recipients of contamination of all sorts.
Tanks are often used for washing of clothes, cattle,
humans, cooking pots and there may be regular
defecation around the edges which will be washed
into the tank. Tanks are thus subjected to unlimited
possibilities of contamination and are highly
dangerous, as a source of drinking water
Improvement of tanks
A certain amount of natural purification does take
place in tank water because of storage, oxidation
and other agencies.
(1)The edges of the tank should be elevated in order
to prevent the entry of surface washings,
(2)There should be a fence around the tank to
prevent access to animals
(3)No one should be permitted to get into the tank
directly.
Improvement of tanks
4) There should be an elevated platform from
where people can draw water,
5) The weeds should be periodically removed,
6) The tank should be cleaned at the end of the
dry season.
Sea water
Though this source is plentiful, it has great many
limitations.
It contains 3.5 per cent of salts in solution.
Desalting and demineralization process
involves heavy expenditure. It is adopted in
places where sea water is the only source
available.
Ground water
Rain water percolating into ground constitutes
ground water.
The advantages of groundwater are:
(1) it is likely to be free from pathogenic agents,
(2) it usually requires no treatment,
(3) the supply is likely to be certain even during dry
season.
(4) It is less subject to contamination than surface
water.
Ground water
The disadvantages are:
(1) it is high in mineral content, e.g., salts of calcium
and magnesium which render the water hard
(2) it requires pumping or some arrangement to lift
the water
WELLS
Wells have been classified into shallow and
deep wells, dug and tube wells.
(1) Shallow wells : Shallow wells tap subsoil water
i.e. the water from above the first impervious
layer in the ground.
(2) Deep wells: A deep well is one which taps
water from the water-bearing stratum below
the first impervious layer in the ground.
WELLS
WELLS
Most of the wells in India are of the shallow type.
Shallow wells are liable to pollution from
neighbouring sources of contamination such as
latrines, urinals, drains, cesspools, soakage pits etc.
They are therefore a health hazard to the
community if they are not made sanitary.
A deep well can also become a health hazard if it
is open, poorly constructed and not protected
against contamination.
WELLS
Wells may also be classified, according to the
method of construction, into Dug wells and Tube
wells.
DUG WELLS
They are the commonest type in India. Two types
of dug wells exist in our rural areas:
(a) the unlined Katcha well and
(b) the Masonry or Pucca well.
Katcha well
Masonry or Pucca well
STEP WELLS
They are a kind of pucca wells.
There is considerable personal contact between
theuser and the water. Some may even wash their
faces, hands and feet
Guineaworm disease is quite a public health
problem in areas where step wells are in use.
The open dug wells and step wells are a health
hazard to the community.
SANITARY WELL
One which is
properly located,
well constructed
and protected
against
contamination
with a view to
yield a supply of
safe water
Construction of sanitary wells
(1) LOCATION
The well should be located not less than 15 m (50
feet) from likely sources of contamination.
Should be located at a higher elevation with
respect to a possible source of contamination.
The well should be so located that no user will
have to carry water for more than 100m.
(2) LINING
The lining of the well should be built of bricks or
stones set in cement up to a depth of at least 6 m
(20 feet) so that water enters from the bottom
and not from the sides of the well.
The lining should be carried 60-90 cm (2-3 feet)
above the ground level.
(3) PARAPET WALL
There should be a parapet wall up to a height of
at least 70-75 cms (28 inches) above the ground.
(4) PLATFORM
There should be a cement-concrete platform
round the well extending at least 1 m (3 feet) in
all directions.
The platform should have gentle slope outwards
towards a drain built along its edges.
(5) DRAIN
There should be a pucca drain to carry off spilled
water to a public drain or a soakage pit
constructed beyond the "cone of filtration" (area
of drainage) of the well.
(6) COVERING
The top of the well should be closed by a
cement concrete cover because the bulk of
the pollution is introduced into the well directly
through the open top.
Open wells cannot be considered sanitary
(7) HAND-PUMP
The well should be equipped with a hand-pump
for lifting the water in a sanitary manner.
The handpump should be of robust construction to
withstand rough handling by the people.
Sanitary wells does not guarantee freedom from
waterborne diseases unless the consumers
observe certain basic precautions at the
individual and family level.
cleanliness should be enforced in the vicinity of
the well.
(8) CONSUMER RESPONSIBILITY
(8) CONSUMER RESPONSIBILITY
Washing of clothes and animals, and the
dumping of refuse and wastes should be
prohibited.
Ropes and buckets from individual homes should
not be used.
Water from the well should be carried in clean
sanitary vessels to individual houses.
(9) QUALITY
The physical, chemical and bacteriological
quality of water should conform to the
acceptable standards of quality of safe and
wholesome water.
TUBE WELLS
water which is bacteriologically safe,
and are also cheap in comparison to
other sources of supply.
The area within 15 m of the tube well
should be kept free from pollution.
An average well may last for a period of
5 to 10 years.
SPRINGS
When ground water
comes to the surface
and flows freely under
natural pressure, it is
called a "spring".
Two types- Shallow
springs and Deep
springs.
WATER PURIFICATION
WATER POLLUTION
Natural and man made impurities
A more serious aspect of water pollution is that
caused by human activity -
Urbanization and Industrialization.
The sources of pollution resulting from
these are :
(a) Sewage: which contains decomposable
organic matter and pathogenic agents.
(b) Industrial and trade wastes: which contain
toxic agents ranging from metal salts to
complex synthetic organic chemicals.
(c) Agricultural pollutants: which comprise
fertilizers and pesticides.
 (d) Physical pollutants: viz heat (thermal
pollution) and radioactive substances.
Indicators of water pollution includes the amount of total suspended
solids,
BOD @ 20ºC, concentration of chlorides, nitrogen & phosphorus &
absence of oxygen.
Water Related diseases
 A. Biological (Water-borne diseases)
1. Those caused by the presence of an infective agent :
(a) Viral : Viral hepatitis A, hepatitis E, poliomyelitis,
rotavirus, diarrhoea in infants
(b) Bacterial : Typhoid and Paratyphoid fever, Bacillary
dysentery, Esch. coli diarrhoea, cholera
(c) Protozoal : Amoebiasis, giardiasis
(d) Helminthic : Roundworm, threadworm, hydatid
disease.
(e) Leptospiral : Weil's disease
2. Those due to the presence of an
aquatic host :
(a) Snail : schistosomiasis
(b) Cyclops : Guinea worm, fish tape worm.
B. Chemical - industrial and agricultural wastes
 These pollutants include detergent solvents,
cyanides, heavy metals, minerals and organic
acids, nitrogenous substances, bleaching
agents, dyes, pigments, sulphides, ammonia,
toxic and biocidal organic compounds.
 Biomagnification of toxins in food chain.
Microplastics !
Purification Of Water
1. Purification of water on a large scale.
2. Purification of water on a small scale.
Purification of water on a large scale
I. Storage.
II. Filtration.
III. Disinfection
1. STORAGE
Natural purification
(a) Physical : By mere storage, the quality of water
improves. About 90 per cent of the suspended
impurities settle down in 24 hours by gravity. The
water becomes clearer. This allows penetration of
light, and reduces the work of the filters.
(b) Chemical : Certain chemical changes also
take place during storage. The aerobic bacteria
oxidize the organic matter present in the water
with the aid of dissolved oxygen. As a result, the
content of free ammonia is reduced and a rise in
nitrates occurs.
 (c) Biological : A tremendous drop takes place in
bacterial count during storage. The pathogenic
organisms gradually die out. It is found that when
river water is stored the total bacterial count drops
by as much as 90 per cent in the first 5-7 days.
1. STORAGE
2. Filtration
98-99 per cent of the bacteria are removed
by filtration, apart from other impurities.
Two types of filters are in use –
1. Biological or slow sand filters.
2. Mechanical or Rapid sand filters.
SLOW SAND OR BIOLOGICAL FILTERS
1. Supernatant (raw) water
2. A bed of graded sand
3. An under-drainage system
4. A system of filter control valves.
Supernatant water
The supernatant water above the sand bed,
whose depth varies from 1 to 1.5M, serves two
important purposes :
It provides a constant head of water so as to
overcome the resistance of the filter bed and
thereby promote the downward flow of water
through the sand bed.
Supernatant water
It provides waiting period of some hours (3
to 12 hours, depending upon the filtration
velocity) for the raw water to undergo
partial purification by sedimentation,
oxidation and particle agglomeration.
The most important part of the filter is the
sand bed.
Thickness of the sand bed -1 metre
Sand grains "effective diameter" between
0.2 and 0.3 mm.
Sand bed
The sand should be clean and free from clay
and organic matter.
The sand bed is supported by a layer of
graded gravel 30-40 cm deep which also
prevents the fine grains being carried into
the drainage pipes.
Sand bed
Water percolates through the sand bed
very slowly (a process taking two hours or
more), and it is subjected to a number of
purification processes.
mechanical straining, sedimentation,
adsorption, oxidation and bacterial
action, all playing their part.
0.1&0.4 𝑀3
/hour/𝑀2
of sand bed.(100-
400L).
Vital layer : When the filter is newly laid, it acts
merely as a mechanical strainer, and cannot truly
be considered as "biological".
But very soon, the surface of the sand bed gets
covered with a slimy growth known as
"Schmutzdecke", vital layer, zoogleal layer or biological
layer.
This layer is slimy and gelatinous and consists of thread
like algae and numerous forms of life including
plankton, diatoms and bacteria.
The formation of vital layer is known as "ripening“ of the
filter.
It may take several days for the vital layer to form
fully, and when fully formed it extends for 2 to 3
cm into the top portion of the sand bed.
The vital layer is the "heart" of the slow sand filter.
It removes organic matter, holds back bacteria
and oxidizes ammoniacal nitrogen into nitrates
and helps in yielding a bacteria-free water.
Until the vital layer is fully formed, the first few
days filtrate is usually run to waste.
It consists of porous or perforated pipes
which serve the dual purpose of providing
an outlet for filtered water, and supporting
the filter medium above.
Once the filter bed has been laid, the
under-drainage system cannot be seen.
Under-drainage system
Filter box : The first 3 elements
(ie.supernatant water, sand bed and under-
drainage system) are contained in the filter
box. The filter box is an open box, usually
rectangular in shape, from 2.5 to 4 metres
deep and is built wholly or partly below
ground. The walls may be made of stone,
brick or cement.
The filter box consists from top to bottom :
Supernatant water 1 to 1.5 metre
Sand bed 1.2 metre
Gravel support 0.30 metre
Filter bottom 0.16 metre
The filter is equipped with certain valves and
devices which are incorporated in the outlet-
pipe system.
The purpose of these devices is to maintain a
constant rate of filtration.
Filter control
An important component of the regulation
system is the "Venturi meter" which measures
the bed resistance or "loss of head". When
the resistance builds up, the operator opens
the regulating valve so as to maintain a
steady rate of filtration.
 When the "loss of head" exceeds 1.3 metre it
is uneconomical to run the filter.
Filter cleaning
Normally the filter may run for weeks or even
months without cleaning.
When the bed resistance increases to such an
extent that the regulating valve has to be kept
fully open, it is time to clean the filter bed, since
any further increase in resistance is bound to
reduce the filtration rate.
At this stage………….
The supernatant water is drained off, and
the sand bed is cleaned by "scraping" off
the top portion of the sand layer to a
depth of 1 or 2 cm.
This operation may be carried out by unskilled
labourers using hand tools or by mechanical
equipment.
After several years of operation, and 20 or 30
scrapings, the thickness of the sand bed will
have reduced to about 0.5 to 0.8 metre.
Then the plant is closed down and a new
bed is constructed.
Advantages of Slow Sand Filter
1. Simple to construct and operate.
2. The cost of construction is cheaper than that
of rapid sand filters.
3. The physical, chemical and bacteriological
quality of filtered water is very high.
 When working ideally, slow sand filters have
been shown to reduce total bacterial counts
by 99.9 to 99.99 per cent and E. coli by 99 to
99. 9 per cent.
RAPID SAND FILTER
Rapid sand filters are of two types,
1. The gravity type (e.g. Paterson's filter)
2. The pressure type (e.g. Candy's filter).
Both the types are in use.
Coagulation
 The raw water is first treated with a chemical
coagulant such as alum, the dose of which
varies from 5 to 40 mg or more per liter,
depending upon the turbidity and colour,
temperature and the pH value of the water.
Rapid mixing
The treated water is then subjected to violent
agitation in a "mixing chamber" for a few
minutes.
This allows a quick and thorough dissemination of
alum throughout the bulk of the water, which is
very necessary.
Flocculation
The next phase involves a slow and gentle
stirring of the treated water in a "flocculation
chamber" for about 30 minutes.
The mechanical type of flocculator is the most
widely used.
It consists of a number of paddles which rotate
at 2 to 4 rpm. The paddles rotate with the help of
motors. This slow and gentle stirring results in the
formation of a thick, copious, white flocculant
precipitate of aluminium hydroxide.
The thicker the precipitate or flock diameter, the
greater the settling velocity.
Flocculation
Sedimentation
The coagulated water is now led into
sedimentation tanks where it is detained for
periods varying from 2-6 hours when the flocculent
precipitate together with impurities and bacteria
settle down in the tank.
At least 95 per cent of the flocculant precipitate
needs to be removed before the water is
admitted into the rapid sand filters.
The precipitate or sludge which settles at
the bottom is removed from time to time
without disturbing the operation of the tank.
 For proper maintenance, the tanks should
be cleaned. regularly from time to time,
otherwise they may become a breeding
ground for molluscs and sponges.
Sedimentation
Filtration
The partly
clarified water
is now
subjected to
rapid sand
filtration.
FILTER BEDS
Each unit of Filter bed has a surface of
about 80 to 90 𝑀2
(about 900 sq. feet).
Sand is the filtering medium.
 The "effective size" of the sand particles is
between 0.4-0. 7 mm.
The depth of the sand bed is usually about
1 metre (2.5 to 3 feet).
Below the sand bed is a layer of graded gravel,
36 to 40 cm. (1-1.5feet) deep.
The gravel supports the sand bed and permits
the filtered water to move freely towards the
under-drains.
 The depth of the water on the top of the sand
bed is 1.0 to 1.5 m (5-6 feet).
The under-drains at the bottom of the filter beds
collect the filtered water. The rate of filtration is 5-
15 𝑀3
/ 𝑀2
/hour. (5000L)
Filtration
As filtration proceeds, the "alum-floc" not
removed by sedimentation is held back on the
sand bed.
It forms a slimy layer comparable to the
zoogleal layer in the· slow sand filters.
It adsorbs bacteria from the water and effects
purification. Oxidation of ammonia also takes
place during the passage of water through the
filters.
As filtration proceeds, the suspended
impurities and bacteria clog the filters.
The filters soon become dirty and begin to
lose their efficiency. When the "loss of head"
approaches 7-8 feet, filtration is stopped and
the filters are subjected to a washing process
known as "backwashing.
Backwashing
Rapid sand filters need frequent washing daily
or weekly, depending upon the loss of head.
Washing is accomplished by reversing the flow
of water through the sand bed, which is called
"backwashing".
Backwashing dislodges the impurities and
cleans up the sand bed.
The washing is stopped when clear sand is
visible and the wash water is sufficiently clear.
The whole process of washing takes about 15
minutes.
In some rapid sand filters, compressed air is
used as part of the backwashing processes.
Backwashing
ADVANTAGES
1. Rapid sand filter can deal with raw water
directly. No preliminary storage is needed
2. The filter beds occupy less space
3. Filtration is rapid, 40-50 times that of a slow
sand filter
4. The washing of the filter is easy.
5. There is more flexibility in operation.
DISINFECTION
Capable of destroying the pathogenic
organisms present, within the contact time
available and not unduly influenced by the
range of physical and chemical properties of
water encountered particularly temperature,
pH and mineral constituents;
Should not leave products of reaction which
render the water toxic or impart colour or
otherwise make it unpotable.
CHLORINATION
Chlorine kills pathogenic bacteria, but is has no
effect on spores and certain viruses (e.g., polio,
viral hepatitis) except in high doses.
Apart from its germicidal effect, chlorine has
several important secondary properties of value
in water treatment : it oxidizes iron, manganese
and hydrogen sulphide; it destroys some taste
and odour producing constituents; it controls
algae and slime organisms; and aids
coagulation.
Action of chlorine
 When chlorine is added to water, there is formation
of hydrochloric and hypochlorous acids.
 The hydrochloric acid is neutralized by the alkalinity
of the water.
 The hypochlorous acid ionizes to form hydrogen ions
and hypochlorite ions, as follows :-
 H2O + Cl2 HCl + HOCl
 HOCl H + OCl
The disinfecting action of chlorine is mainly
due to the hypochlorous acid, and to a small
extent due to the hypochlorite ions.
The hypochlorous acid (HClO) is the most
effective form of chlorine for water
disinfection.
It is more effective (70-80 times) than the
hypochlorite ion.
Principles of chlorination
Water to be chlorinated should be clear and
free from turbidity.
Estimate the chlorine demand of water
The contact period - The presence of free
residual chlorine for a contact period of at least
one hour is essential to kill bacteria and viruses
The minimum recommended concentration of
free chlorine is 0.5 mg/L for one hour.
The free residual chlorine provides a margin of
safety against subsequent microbial
contamination such as may occur during storage
and distribution.
The sum of the chlorine demand of the specific
water plus the free residual chlorine of 0.5 mg/L
constitutes the correct dose of chlorine to be
applied.
CHLORINE DEMAND
 "The chlorine demand of water is the difference
between the amount of chlorine added to the water,
and the amount of residual chlorine remaining at the
end of a specific period of contact (usually 60 minutes),
at a given temperature and pH of the water".
 In other words, it is the amount of chlorine that is
needed to destroy bacteria, and to oxidize all the
organic matter and ammoniacal substances present in
the water.
 The point at which the chlorine demand of the water is
met is called the "break-point"
METHODS OF CHLORINATION
For disinfecting large bodies of water,
chlorine is applied either as
1. chlorine gas
2. chloramine
3. perchloron.
CHLORINE GAS
 Chlorine gas is the first choice, because it is
cheap, quick in action, efficient and easy to
apply.
 Since chlorine gas is an irritant to the eyes and
poisonous, a special equipment known as
"chlorinating equipment" is required to apply
chlorine gas to water supplies.
 Paterson's chloronome is one such device for
measuring, regulating and administering
gaseous chlorine to water supplies.
CHLORAMINES
Chloramines are loose compounds of
chlorine and ammonia.
They have a less tendency to produce
chlorinous tastes and give a more persistent
type of residual chlorine.
The greatest drawback of chloramines is that
they have a slower action than chlorine and
therefore they are not being used to any
great extent in water treatment.
Perchloron or high test
hypochlorite (H.T.H.)
Perchloron or high test hypochlorite
(H.T.H.) is a calcium compound which
carries 60-70 per cent of available
chlorine.
 Solutions prepared from H.T.H. are also
used for water disinfection.
PURIFICATION OF WATER ON A
SMALL SCALE
Household purification of water –
BOILING
CHEMICAL DISINFECTION
Bleaching powder
Chlorine solution
High test hypochlorite
Chlorine tablets
Iodine
Potassium permanganate
 FILTRATION - Water can be purified on a small scale
by filtering through ceramic filters such as Pasteur
Chamberland filter, Berkefeld filter and "Katadyn"
filter.
 ULTRAVIOLET IRRADIATION - exposure of a film of
water, upto about 120 mm thick, to one or several
quartz mercury vapour arc lamps emitting
ultraviolet radiation at a wavelength of 254 (Nano-
metre).
Disinfection of wells –
 The most effective and cheapest method of
disinfecting wells is by bleaching powder.
HARDNESS
Hardness may be defined as the soap
destroying power of water.
The hardness in water is caused mainly by four
dissolved compounds. These are
1. Calcium bicarbonate
2. Magnesium bicarbonate
3. Calcium sulphate, and
4. Magnesium sulphate.
types
Temporary hardness - due to the
presence of calcium and magnesium
bicarbonates.
Permanent hardness - due to calcium
and magnesium sulphates, chlorides
and nitrates.
Hardness in water is expressed in
terms of "milliequivalents per litre
(mEq/L)".
Drinking water should be moderately
hard.
Softening of water is recommended
when the hardness exceeds 3 mEq/l
(150 mg per litre).
DISADVANTAGES OF
HARDNESS
1.Hardness in water consumes more soap and
detergents.
2.When hard water is heated, the carbonates
are precipitated and bring about furring or
scaling of boilers. This leads to great fuel
consumption, loss of efficiency and may
sometimes cause boiler explosions.
3. Hard water adversely affects cooking; food
cooked in soft water retains its natural colour
and appearance.
4. Fabrics washed with soap in hard water do not
have a long life.
5. There are many industrial processes in which
hard water is unsuited and gives rise to
economic losses.
6. Hardness shortens the life of pipes and fixtures.
Removal of hardness
Temporary hardness
(a) Boiling
(b) Addition of lime
(c) Addition of sodium carbonate
(d) Permutit process.
Permanent hardness
(a) Addition of sodium carbonate
(b) Base exchange process.
BOILING
Boiling removes the temporary hardness by
expelling carbon dioxide, and precipitating
the insoluble calcium carbonate.
It is an expensive method to soften water on
a large scale.
Ca(HC03)2 -- CaC03 + H2O + C02
ADDITION OF LIME
 Lime absorbs the carbon dioxide, and
precipitates the insoluble calcium
carbonate.
 Ca (OH)2 + Ca(HC03) 2 2CaC03
+ 2H2O
ADDITION OF SODIUM
CARBONATE
 Sodium carbonate (soda ash) removes
both temporary and permanent hardness,
 (i) Na2 C03 + Ca(HC03)2 2NaHC03 +
CaC03
 (ii) CaS04 + Na2 C03 CaC03 + Na2 S04
BASE EXCHANGE PROCESS
In the treatment of large water supplies, the
permutit process is used.
Sodium permutit is a complex compound of
sodium, aluminium and siilica (Na2 Al2 Si20 H20).
It has the property of exchanging the sodium
cation for the calcium and magnesium ions in
the water.
 When hard water is passed through the permutit
the calcium and magnesium ions are entirely
removed by base exchange and the sodium
permutit is finally converted into calcium and
magnesium permutit.
 By this process, water can be softened to zero
hardness.
 Permutit process removes both temporary and
permanent hardness.
JALA
TYPES
Susrutha – Anthariksha jala / rain water
Bhauma jala/ ground water
Antariksh jala – 4
Dhara – falling
Kara – water from hailstones
Taushara – water from dew
Haima – water from melting of snow
Divya Jala
There are different types of water
mentioned, but Charakacharya considers
only one type of Jala; which falls from sky
in the form of rain. Such water in the form
of rain is known as Divya Jala and it is
Sheeta, clean, sacred, devoid of impurities.
तत् पतत् पतततं चैव देशकालावपेक्षते|| शीतं शुतच तशवं मृ 􀄶ंं तवमलं लघु
षड्गुणम्| प्रकृत्या तदव्यमुदकं ,...(C.S.S.27/198)

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Water

  • 2. In 1981, the 34th World Health Assembly in a resolution emphasized that safe drinking water is a basic element of "primary health care" which is the key to the attainment of "Health for All by the year 2000 AD". Water is integrated with other PHC components because it is an essential part of health education, food and nutrition, and also MCH
  • 3. Safe and wholesome water  This has been defined as water that is a) free from pathogenic agents b) free from harmful chemical substances c) pleasant to the taste, i.e., free from colour and odour; d) usable for domestic purposes. Water is said to be polluted or contaminated when it does not fulfil the above criteria.
  • 4. Water requirement Physiological requirements for drinking water have been estimated at about 2 litres per head per day (just for survival). A daily supply of 150-200 litres per capita is considered as an adequate supply to meet the needs for all urban domestic purposes. In India 40 litres of water supply per capita per day was the set target.
  • 5. Uses of water (1) Domestic use : on domestic front, water is required for drinking, cooking, washing and bathing, flushing of toilets, gardening etc. (2) Public purposes : cleaning streets, recreational purposes like swimming pools, public fountains and ornamental ponds, fire protection and public parks. (3) Industrial purposes : for processing and cooling;
  • 6. Uses of water (4) Agricultural purpose : irrigation (5) Power production from hydropower and steam power; (6) Carrying away waste from all manner of establishments and institutions.
  • 7. Sources of water supply In general, water sources must conform to two criteria : (a)the quantity must be sufficient to meet present and future requirement (b)the quality of water must be acceptable. There are three main sources of water
  • 8. Sources of water supply 1. RAIN 2. SURFACE WATER 3. GROUND WATER Impounding reservoirs Rivers and streams Tanks, ponds and lakes Shallow wells Deep wells Springs
  • 9. Rain Rain is the prime source of all water. CHARACTERISTICS : Rain water is the purest water in nature. Physically, it . is clear, bright and sparkling. Chemically, it is very soft water containing only traces of dissolved solids and free from pathogenic agents.
  • 10. Rain IMPURITIES : Rain water tends to become impure as it passes through. the atmosphere. It picks up suspended impurities from the atmosphere· such as dust, soot and microorganisms and gases such as carbon dioxide, nitrogen, oxygen and ammonia.
  • 11. Surface water Surface water originates from rain water. It is the main source of water supply in many areas. Surface water is prone to contamination from human and animal sources. As such it is never safe for human consumption unless subjected to sanitary protection and purification before use.
  • 12. surface water sources (1) Impounding Reservoirs. (2) Rivers and Streams, (3) Tanks, Ponds and Lakes. In general, surface water supplies possess a high probability of organic, bacterial and viral contamination.
  • 13. IMPOUNDING RESERVOIRS These are artificial lakes constructed usually of earthwork or masonry in which large quantities of surface water is stored. Dams built across rivers and mountain streams also provide large reserves of surface water. The area draining into the reservoir is called "Catchment area". One disadvantage of storing water for long periods in reservoirs is the growth of algae and other microscopic organisms, which impart bad tastes and odours to water.
  • 14.
  • 15. IMPOUNDING RESERVOIRS CHARACTERISTICS : Impounding reservoirs usually furnish a fairly good quality of water. Water is usually clear, palatable and ranks next to rain water. The water is usually soft and considered to be free of pathogenic organisms. IMPURITIES : The upland surface water derives its impurities from the catchment area, the sources being human habitations and animal keeping or grazing.
  • 16. RIVERS Many rivers furnish a dependable supply of water. The chief drawback of river water is that it is always grossly polluted and is quite unfit for drinking without treatment. CHARACTERISTICS : River water is turbid during rainy season; it may be clear in other seasons. The bacterial count, including the human intestinal organisms may be very high.
  • 17. RIVERS IMPURITIES : Rivers are described as a direct connection between the alimentary canal of the people living upstream and the mouths of those below. Impurities of river water are derived from surface washings, sewage and sullage water, industrial and trade wastes, and drainage from agricultural areas.
  • 18. RIVERS SELF-PURIFICATION : Certain amount of self- purification does occur in river water by natural forces of purification such as dilution, sedimentation, aeration, oxidation, sunlight, plant and animal life but these agencies are not sufficient to render the water potable. River water needs purification before it can be used for drinking purposes.
  • 19.
  • 20. TANKS Tanks are large excavations in which surface water is stored. They are an important source of water supply in some Indian villages. Tanks are recipients of contamination of all sorts. Tanks are often used for washing of clothes, cattle, humans, cooking pots and there may be regular defecation around the edges which will be washed into the tank. Tanks are thus subjected to unlimited possibilities of contamination and are highly dangerous, as a source of drinking water
  • 21.
  • 22. Improvement of tanks A certain amount of natural purification does take place in tank water because of storage, oxidation and other agencies. (1)The edges of the tank should be elevated in order to prevent the entry of surface washings, (2)There should be a fence around the tank to prevent access to animals (3)No one should be permitted to get into the tank directly.
  • 23. Improvement of tanks 4) There should be an elevated platform from where people can draw water, 5) The weeds should be periodically removed, 6) The tank should be cleaned at the end of the dry season.
  • 24.
  • 25. Sea water Though this source is plentiful, it has great many limitations. It contains 3.5 per cent of salts in solution. Desalting and demineralization process involves heavy expenditure. It is adopted in places where sea water is the only source available.
  • 26. Ground water Rain water percolating into ground constitutes ground water. The advantages of groundwater are: (1) it is likely to be free from pathogenic agents, (2) it usually requires no treatment, (3) the supply is likely to be certain even during dry season. (4) It is less subject to contamination than surface water.
  • 27. Ground water The disadvantages are: (1) it is high in mineral content, e.g., salts of calcium and magnesium which render the water hard (2) it requires pumping or some arrangement to lift the water
  • 28. WELLS Wells have been classified into shallow and deep wells, dug and tube wells. (1) Shallow wells : Shallow wells tap subsoil water i.e. the water from above the first impervious layer in the ground. (2) Deep wells: A deep well is one which taps water from the water-bearing stratum below the first impervious layer in the ground.
  • 29.
  • 30. WELLS
  • 31. WELLS Most of the wells in India are of the shallow type. Shallow wells are liable to pollution from neighbouring sources of contamination such as latrines, urinals, drains, cesspools, soakage pits etc. They are therefore a health hazard to the community if they are not made sanitary. A deep well can also become a health hazard if it is open, poorly constructed and not protected against contamination.
  • 32. WELLS Wells may also be classified, according to the method of construction, into Dug wells and Tube wells. DUG WELLS They are the commonest type in India. Two types of dug wells exist in our rural areas: (a) the unlined Katcha well and (b) the Masonry or Pucca well.
  • 35. STEP WELLS They are a kind of pucca wells. There is considerable personal contact between theuser and the water. Some may even wash their faces, hands and feet Guineaworm disease is quite a public health problem in areas where step wells are in use. The open dug wells and step wells are a health hazard to the community.
  • 36.
  • 37. SANITARY WELL One which is properly located, well constructed and protected against contamination with a view to yield a supply of safe water
  • 39. (1) LOCATION The well should be located not less than 15 m (50 feet) from likely sources of contamination. Should be located at a higher elevation with respect to a possible source of contamination. The well should be so located that no user will have to carry water for more than 100m.
  • 40. (2) LINING The lining of the well should be built of bricks or stones set in cement up to a depth of at least 6 m (20 feet) so that water enters from the bottom and not from the sides of the well. The lining should be carried 60-90 cm (2-3 feet) above the ground level.
  • 41. (3) PARAPET WALL There should be a parapet wall up to a height of at least 70-75 cms (28 inches) above the ground. (4) PLATFORM There should be a cement-concrete platform round the well extending at least 1 m (3 feet) in all directions. The platform should have gentle slope outwards towards a drain built along its edges.
  • 42. (5) DRAIN There should be a pucca drain to carry off spilled water to a public drain or a soakage pit constructed beyond the "cone of filtration" (area of drainage) of the well. (6) COVERING The top of the well should be closed by a cement concrete cover because the bulk of the pollution is introduced into the well directly through the open top. Open wells cannot be considered sanitary
  • 43. (7) HAND-PUMP The well should be equipped with a hand-pump for lifting the water in a sanitary manner. The handpump should be of robust construction to withstand rough handling by the people.
  • 44. Sanitary wells does not guarantee freedom from waterborne diseases unless the consumers observe certain basic precautions at the individual and family level. cleanliness should be enforced in the vicinity of the well. (8) CONSUMER RESPONSIBILITY
  • 45. (8) CONSUMER RESPONSIBILITY Washing of clothes and animals, and the dumping of refuse and wastes should be prohibited. Ropes and buckets from individual homes should not be used. Water from the well should be carried in clean sanitary vessels to individual houses.
  • 46. (9) QUALITY The physical, chemical and bacteriological quality of water should conform to the acceptable standards of quality of safe and wholesome water.
  • 47. TUBE WELLS water which is bacteriologically safe, and are also cheap in comparison to other sources of supply. The area within 15 m of the tube well should be kept free from pollution. An average well may last for a period of 5 to 10 years.
  • 48. SPRINGS When ground water comes to the surface and flows freely under natural pressure, it is called a "spring". Two types- Shallow springs and Deep springs.
  • 50. WATER POLLUTION Natural and man made impurities A more serious aspect of water pollution is that caused by human activity - Urbanization and Industrialization.
  • 51. The sources of pollution resulting from these are : (a) Sewage: which contains decomposable organic matter and pathogenic agents. (b) Industrial and trade wastes: which contain toxic agents ranging from metal salts to complex synthetic organic chemicals.
  • 52. (c) Agricultural pollutants: which comprise fertilizers and pesticides.  (d) Physical pollutants: viz heat (thermal pollution) and radioactive substances. Indicators of water pollution includes the amount of total suspended solids, BOD @ 20ºC, concentration of chlorides, nitrogen & phosphorus & absence of oxygen.
  • 53. Water Related diseases  A. Biological (Water-borne diseases) 1. Those caused by the presence of an infective agent : (a) Viral : Viral hepatitis A, hepatitis E, poliomyelitis, rotavirus, diarrhoea in infants (b) Bacterial : Typhoid and Paratyphoid fever, Bacillary dysentery, Esch. coli diarrhoea, cholera (c) Protozoal : Amoebiasis, giardiasis (d) Helminthic : Roundworm, threadworm, hydatid disease. (e) Leptospiral : Weil's disease
  • 54. 2. Those due to the presence of an aquatic host : (a) Snail : schistosomiasis (b) Cyclops : Guinea worm, fish tape worm.
  • 55. B. Chemical - industrial and agricultural wastes  These pollutants include detergent solvents, cyanides, heavy metals, minerals and organic acids, nitrogenous substances, bleaching agents, dyes, pigments, sulphides, ammonia, toxic and biocidal organic compounds.  Biomagnification of toxins in food chain. Microplastics !
  • 56. Purification Of Water 1. Purification of water on a large scale. 2. Purification of water on a small scale.
  • 57. Purification of water on a large scale I. Storage. II. Filtration. III. Disinfection
  • 58. 1. STORAGE Natural purification (a) Physical : By mere storage, the quality of water improves. About 90 per cent of the suspended impurities settle down in 24 hours by gravity. The water becomes clearer. This allows penetration of light, and reduces the work of the filters. (b) Chemical : Certain chemical changes also take place during storage. The aerobic bacteria oxidize the organic matter present in the water with the aid of dissolved oxygen. As a result, the content of free ammonia is reduced and a rise in nitrates occurs.
  • 59.  (c) Biological : A tremendous drop takes place in bacterial count during storage. The pathogenic organisms gradually die out. It is found that when river water is stored the total bacterial count drops by as much as 90 per cent in the first 5-7 days. 1. STORAGE
  • 60. 2. Filtration 98-99 per cent of the bacteria are removed by filtration, apart from other impurities. Two types of filters are in use – 1. Biological or slow sand filters. 2. Mechanical or Rapid sand filters.
  • 61. SLOW SAND OR BIOLOGICAL FILTERS 1. Supernatant (raw) water 2. A bed of graded sand 3. An under-drainage system 4. A system of filter control valves.
  • 62.
  • 63. Supernatant water The supernatant water above the sand bed, whose depth varies from 1 to 1.5M, serves two important purposes : It provides a constant head of water so as to overcome the resistance of the filter bed and thereby promote the downward flow of water through the sand bed.
  • 64. Supernatant water It provides waiting period of some hours (3 to 12 hours, depending upon the filtration velocity) for the raw water to undergo partial purification by sedimentation, oxidation and particle agglomeration.
  • 65. The most important part of the filter is the sand bed. Thickness of the sand bed -1 metre Sand grains "effective diameter" between 0.2 and 0.3 mm. Sand bed
  • 66. The sand should be clean and free from clay and organic matter. The sand bed is supported by a layer of graded gravel 30-40 cm deep which also prevents the fine grains being carried into the drainage pipes. Sand bed
  • 67.
  • 68. Water percolates through the sand bed very slowly (a process taking two hours or more), and it is subjected to a number of purification processes. mechanical straining, sedimentation, adsorption, oxidation and bacterial action, all playing their part. 0.1&0.4 𝑀3 /hour/𝑀2 of sand bed.(100- 400L).
  • 69. Vital layer : When the filter is newly laid, it acts merely as a mechanical strainer, and cannot truly be considered as "biological". But very soon, the surface of the sand bed gets covered with a slimy growth known as "Schmutzdecke", vital layer, zoogleal layer or biological layer. This layer is slimy and gelatinous and consists of thread like algae and numerous forms of life including plankton, diatoms and bacteria. The formation of vital layer is known as "ripening“ of the filter.
  • 70. It may take several days for the vital layer to form fully, and when fully formed it extends for 2 to 3 cm into the top portion of the sand bed. The vital layer is the "heart" of the slow sand filter. It removes organic matter, holds back bacteria and oxidizes ammoniacal nitrogen into nitrates and helps in yielding a bacteria-free water. Until the vital layer is fully formed, the first few days filtrate is usually run to waste.
  • 71. It consists of porous or perforated pipes which serve the dual purpose of providing an outlet for filtered water, and supporting the filter medium above. Once the filter bed has been laid, the under-drainage system cannot be seen. Under-drainage system
  • 72. Filter box : The first 3 elements (ie.supernatant water, sand bed and under- drainage system) are contained in the filter box. The filter box is an open box, usually rectangular in shape, from 2.5 to 4 metres deep and is built wholly or partly below ground. The walls may be made of stone, brick or cement.
  • 73. The filter box consists from top to bottom : Supernatant water 1 to 1.5 metre Sand bed 1.2 metre Gravel support 0.30 metre Filter bottom 0.16 metre
  • 74. The filter is equipped with certain valves and devices which are incorporated in the outlet- pipe system. The purpose of these devices is to maintain a constant rate of filtration. Filter control
  • 75. An important component of the regulation system is the "Venturi meter" which measures the bed resistance or "loss of head". When the resistance builds up, the operator opens the regulating valve so as to maintain a steady rate of filtration.  When the "loss of head" exceeds 1.3 metre it is uneconomical to run the filter.
  • 76. Filter cleaning Normally the filter may run for weeks or even months without cleaning. When the bed resistance increases to such an extent that the regulating valve has to be kept fully open, it is time to clean the filter bed, since any further increase in resistance is bound to reduce the filtration rate. At this stage………….
  • 77. The supernatant water is drained off, and the sand bed is cleaned by "scraping" off the top portion of the sand layer to a depth of 1 or 2 cm.
  • 78. This operation may be carried out by unskilled labourers using hand tools or by mechanical equipment. After several years of operation, and 20 or 30 scrapings, the thickness of the sand bed will have reduced to about 0.5 to 0.8 metre. Then the plant is closed down and a new bed is constructed.
  • 79. Advantages of Slow Sand Filter 1. Simple to construct and operate. 2. The cost of construction is cheaper than that of rapid sand filters. 3. The physical, chemical and bacteriological quality of filtered water is very high.  When working ideally, slow sand filters have been shown to reduce total bacterial counts by 99.9 to 99.99 per cent and E. coli by 99 to 99. 9 per cent.
  • 80. RAPID SAND FILTER Rapid sand filters are of two types, 1. The gravity type (e.g. Paterson's filter) 2. The pressure type (e.g. Candy's filter). Both the types are in use.
  • 81.
  • 82. Coagulation  The raw water is first treated with a chemical coagulant such as alum, the dose of which varies from 5 to 40 mg or more per liter, depending upon the turbidity and colour, temperature and the pH value of the water.
  • 83. Rapid mixing The treated water is then subjected to violent agitation in a "mixing chamber" for a few minutes. This allows a quick and thorough dissemination of alum throughout the bulk of the water, which is very necessary.
  • 84.
  • 85. Flocculation The next phase involves a slow and gentle stirring of the treated water in a "flocculation chamber" for about 30 minutes. The mechanical type of flocculator is the most widely used.
  • 86. It consists of a number of paddles which rotate at 2 to 4 rpm. The paddles rotate with the help of motors. This slow and gentle stirring results in the formation of a thick, copious, white flocculant precipitate of aluminium hydroxide. The thicker the precipitate or flock diameter, the greater the settling velocity. Flocculation
  • 87.
  • 88. Sedimentation The coagulated water is now led into sedimentation tanks where it is detained for periods varying from 2-6 hours when the flocculent precipitate together with impurities and bacteria settle down in the tank. At least 95 per cent of the flocculant precipitate needs to be removed before the water is admitted into the rapid sand filters.
  • 89. The precipitate or sludge which settles at the bottom is removed from time to time without disturbing the operation of the tank.  For proper maintenance, the tanks should be cleaned. regularly from time to time, otherwise they may become a breeding ground for molluscs and sponges. Sedimentation
  • 90. Filtration The partly clarified water is now subjected to rapid sand filtration.
  • 91.
  • 92. FILTER BEDS Each unit of Filter bed has a surface of about 80 to 90 𝑀2 (about 900 sq. feet). Sand is the filtering medium.  The "effective size" of the sand particles is between 0.4-0. 7 mm. The depth of the sand bed is usually about 1 metre (2.5 to 3 feet).
  • 93. Below the sand bed is a layer of graded gravel, 36 to 40 cm. (1-1.5feet) deep. The gravel supports the sand bed and permits the filtered water to move freely towards the under-drains.  The depth of the water on the top of the sand bed is 1.0 to 1.5 m (5-6 feet). The under-drains at the bottom of the filter beds collect the filtered water. The rate of filtration is 5- 15 𝑀3 / 𝑀2 /hour. (5000L)
  • 94. Filtration As filtration proceeds, the "alum-floc" not removed by sedimentation is held back on the sand bed. It forms a slimy layer comparable to the zoogleal layer in the· slow sand filters. It adsorbs bacteria from the water and effects purification. Oxidation of ammonia also takes place during the passage of water through the filters.
  • 95. As filtration proceeds, the suspended impurities and bacteria clog the filters. The filters soon become dirty and begin to lose their efficiency. When the "loss of head" approaches 7-8 feet, filtration is stopped and the filters are subjected to a washing process known as "backwashing.
  • 96. Backwashing Rapid sand filters need frequent washing daily or weekly, depending upon the loss of head. Washing is accomplished by reversing the flow of water through the sand bed, which is called "backwashing". Backwashing dislodges the impurities and cleans up the sand bed.
  • 97. The washing is stopped when clear sand is visible and the wash water is sufficiently clear. The whole process of washing takes about 15 minutes. In some rapid sand filters, compressed air is used as part of the backwashing processes. Backwashing
  • 98.
  • 99. ADVANTAGES 1. Rapid sand filter can deal with raw water directly. No preliminary storage is needed 2. The filter beds occupy less space 3. Filtration is rapid, 40-50 times that of a slow sand filter 4. The washing of the filter is easy. 5. There is more flexibility in operation.
  • 100.
  • 101. DISINFECTION Capable of destroying the pathogenic organisms present, within the contact time available and not unduly influenced by the range of physical and chemical properties of water encountered particularly temperature, pH and mineral constituents; Should not leave products of reaction which render the water toxic or impart colour or otherwise make it unpotable.
  • 102. CHLORINATION Chlorine kills pathogenic bacteria, but is has no effect on spores and certain viruses (e.g., polio, viral hepatitis) except in high doses. Apart from its germicidal effect, chlorine has several important secondary properties of value in water treatment : it oxidizes iron, manganese and hydrogen sulphide; it destroys some taste and odour producing constituents; it controls algae and slime organisms; and aids coagulation.
  • 103. Action of chlorine  When chlorine is added to water, there is formation of hydrochloric and hypochlorous acids.  The hydrochloric acid is neutralized by the alkalinity of the water.  The hypochlorous acid ionizes to form hydrogen ions and hypochlorite ions, as follows :-  H2O + Cl2 HCl + HOCl  HOCl H + OCl
  • 104. The disinfecting action of chlorine is mainly due to the hypochlorous acid, and to a small extent due to the hypochlorite ions. The hypochlorous acid (HClO) is the most effective form of chlorine for water disinfection. It is more effective (70-80 times) than the hypochlorite ion.
  • 105. Principles of chlorination Water to be chlorinated should be clear and free from turbidity. Estimate the chlorine demand of water The contact period - The presence of free residual chlorine for a contact period of at least one hour is essential to kill bacteria and viruses
  • 106. The minimum recommended concentration of free chlorine is 0.5 mg/L for one hour. The free residual chlorine provides a margin of safety against subsequent microbial contamination such as may occur during storage and distribution. The sum of the chlorine demand of the specific water plus the free residual chlorine of 0.5 mg/L constitutes the correct dose of chlorine to be applied.
  • 107. CHLORINE DEMAND  "The chlorine demand of water is the difference between the amount of chlorine added to the water, and the amount of residual chlorine remaining at the end of a specific period of contact (usually 60 minutes), at a given temperature and pH of the water".  In other words, it is the amount of chlorine that is needed to destroy bacteria, and to oxidize all the organic matter and ammoniacal substances present in the water.  The point at which the chlorine demand of the water is met is called the "break-point"
  • 108. METHODS OF CHLORINATION For disinfecting large bodies of water, chlorine is applied either as 1. chlorine gas 2. chloramine 3. perchloron.
  • 109. CHLORINE GAS  Chlorine gas is the first choice, because it is cheap, quick in action, efficient and easy to apply.  Since chlorine gas is an irritant to the eyes and poisonous, a special equipment known as "chlorinating equipment" is required to apply chlorine gas to water supplies.  Paterson's chloronome is one such device for measuring, regulating and administering gaseous chlorine to water supplies.
  • 110. CHLORAMINES Chloramines are loose compounds of chlorine and ammonia. They have a less tendency to produce chlorinous tastes and give a more persistent type of residual chlorine. The greatest drawback of chloramines is that they have a slower action than chlorine and therefore they are not being used to any great extent in water treatment.
  • 111. Perchloron or high test hypochlorite (H.T.H.) Perchloron or high test hypochlorite (H.T.H.) is a calcium compound which carries 60-70 per cent of available chlorine.  Solutions prepared from H.T.H. are also used for water disinfection.
  • 112. PURIFICATION OF WATER ON A SMALL SCALE Household purification of water – BOILING CHEMICAL DISINFECTION Bleaching powder Chlorine solution High test hypochlorite Chlorine tablets Iodine Potassium permanganate
  • 113.  FILTRATION - Water can be purified on a small scale by filtering through ceramic filters such as Pasteur Chamberland filter, Berkefeld filter and "Katadyn" filter.  ULTRAVIOLET IRRADIATION - exposure of a film of water, upto about 120 mm thick, to one or several quartz mercury vapour arc lamps emitting ultraviolet radiation at a wavelength of 254 (Nano- metre). Disinfection of wells –  The most effective and cheapest method of disinfecting wells is by bleaching powder.
  • 114. HARDNESS Hardness may be defined as the soap destroying power of water. The hardness in water is caused mainly by four dissolved compounds. These are 1. Calcium bicarbonate 2. Magnesium bicarbonate 3. Calcium sulphate, and 4. Magnesium sulphate.
  • 115. types Temporary hardness - due to the presence of calcium and magnesium bicarbonates. Permanent hardness - due to calcium and magnesium sulphates, chlorides and nitrates.
  • 116. Hardness in water is expressed in terms of "milliequivalents per litre (mEq/L)". Drinking water should be moderately hard. Softening of water is recommended when the hardness exceeds 3 mEq/l (150 mg per litre).
  • 117. DISADVANTAGES OF HARDNESS 1.Hardness in water consumes more soap and detergents. 2.When hard water is heated, the carbonates are precipitated and bring about furring or scaling of boilers. This leads to great fuel consumption, loss of efficiency and may sometimes cause boiler explosions.
  • 118. 3. Hard water adversely affects cooking; food cooked in soft water retains its natural colour and appearance. 4. Fabrics washed with soap in hard water do not have a long life. 5. There are many industrial processes in which hard water is unsuited and gives rise to economic losses. 6. Hardness shortens the life of pipes and fixtures.
  • 119. Removal of hardness Temporary hardness (a) Boiling (b) Addition of lime (c) Addition of sodium carbonate (d) Permutit process. Permanent hardness (a) Addition of sodium carbonate (b) Base exchange process.
  • 120. BOILING Boiling removes the temporary hardness by expelling carbon dioxide, and precipitating the insoluble calcium carbonate. It is an expensive method to soften water on a large scale. Ca(HC03)2 -- CaC03 + H2O + C02
  • 121. ADDITION OF LIME  Lime absorbs the carbon dioxide, and precipitates the insoluble calcium carbonate.  Ca (OH)2 + Ca(HC03) 2 2CaC03 + 2H2O
  • 122. ADDITION OF SODIUM CARBONATE  Sodium carbonate (soda ash) removes both temporary and permanent hardness,  (i) Na2 C03 + Ca(HC03)2 2NaHC03 + CaC03  (ii) CaS04 + Na2 C03 CaC03 + Na2 S04
  • 123. BASE EXCHANGE PROCESS In the treatment of large water supplies, the permutit process is used. Sodium permutit is a complex compound of sodium, aluminium and siilica (Na2 Al2 Si20 H20). It has the property of exchanging the sodium cation for the calcium and magnesium ions in the water.
  • 124.  When hard water is passed through the permutit the calcium and magnesium ions are entirely removed by base exchange and the sodium permutit is finally converted into calcium and magnesium permutit.  By this process, water can be softened to zero hardness.  Permutit process removes both temporary and permanent hardness.
  • 125. JALA
  • 126. TYPES Susrutha – Anthariksha jala / rain water Bhauma jala/ ground water Antariksh jala – 4 Dhara – falling Kara – water from hailstones Taushara – water from dew Haima – water from melting of snow
  • 127. Divya Jala There are different types of water mentioned, but Charakacharya considers only one type of Jala; which falls from sky in the form of rain. Such water in the form of rain is known as Divya Jala and it is Sheeta, clean, sacred, devoid of impurities. तत् पतत् पतततं चैव देशकालावपेक्षते|| शीतं शुतच तशवं मृ 􀄶ंं तवमलं लघु षड्गुणम्| प्रकृत्या तदव्यमुदकं ,...(C.S.S.27/198)

Editor's Notes

  1. The optimum period of storage of river water is considered to be about 10-14 days. If the water is stored for long periods, there is likelihood of development of vegetable growths such as algae which impart a bad smell and colour to water.
  2. At the bottom of the filter bed is the under-drainage system.