Water Pollution
Water pollution refers to the alteration in the physical, chemical and biological
characterization of water which will cause harmful effects on human, and
aquatic biota and disturb the normal use of water for irrigation, agriculture,
public water supply and industrial use.
Types of water pollution: -
1. Physical pollution of water – It is related to changes in colour, odour, taste,
density, turbidity and thermal pollution.
i) Colour- Colour affects the quality of light that penetrates to a given
depth, and inhibits plant and animal metabolism. Colours are generally
due to organic dye and inorganic complexes. Trade effluents, and
tannary waste, are responsible for deep green or blue colouration of
water which makes it unsuitable for various purposes.
ii) Turbidity- Turbidity arises from colloidal matter, finely suspended
particles and soil erosion. It is due to sewage and industrial effluents.
These are mainly from anthropogenic activities caused by human
beings. Non-turbid polluted water bodies may be contaminated with
acids and alkali, and thus it is also unsuitable for industrial and
domestic uses.
iii) Taste- Change in taste is generally due to industrial effluents and the
main reason for taste change is Fe, Mn, phenols, free chlorine, oils,
hydrocarbons, chlorophenols, petroleum products, synthetic
detergents, pesticides, decomposed organic matter, algae, fungi,
bacteria, and pathogens. They impart a peculiar taste in water bodies.
Water purification techniques like chlorination, fluorination, chemical
precipitation, and activated carbon are used for purification of taste.
iv) Odour- Change in odour is caused due to chemical as well as
biological agents:-
Chemical agents include H2S, free chlorine, NH3, phenols, alcohols, esters,
and hydrocarbons.
Biological agents include algae, fungi, and microorganisms.
Untreated sewage if discharged into water bodies, causes foul odour.
Anaerobic algae cause grassy odour. Rivularia causes muddy odour.
Protozoa causes a fishy odour. Organic amines also cause fishy odour.
Phosphorous compounds cause a vermin smell. Earthy odours are due to
human beings.
Odours can be eliminated by chlorine, activated carbon and aeration.
v) Thermal Pollution- Thermal pollution arises mainly by the
discharge of unutilized heat produced in various thermal power plants, it
reduces the amount of dissolved oxygen due to which organic matter
degrades faster.
2. Chemical pollution of water:- In this category, it causes changes in
acidity, alkalinity, pH, dissolved oxygen and other gases in water. It can be
caused by both organic and inorganic pollutants.
Organic Pollutant:
i) Biodegradable pollutants: These pollutants can be degraded with
time. These includes proteins, domestic sewage, waste from cannery
and slaughterhouses, fats from sewage soap production, food
processing and wool processing, carbohydrates, sugar, starch, from
textile mills, paper mills, sewage, polymers, resins, coal, oil and other
organic substances which are found in domestic and industrial waste.
ii) Non- biodegradable pollutants: These pollutants persist in the
aquatic system for a long period. Pesticides, Herbicides, fungicides, and
insecticides, due to agricultural run-off or from rain that can be washed
into nearby water bodies.
3. Biological Pollution of water:- It is caused by excretory products of warm-
blooded mammals, birds, bacteria, viruses, algae, protozoans, rotifers, etc.
Infection of the intestinal tract, dysentery, cholera, typhoid, polio,
gastroenteritis, infectious hepatitis.
4. Physiological pollution of water:- This is caused by several chemical
agents such as Cl2, F2, SO2, H2S, ketone, phenols, amines, mercaptans, and
hydroxyl benzene. They affect the central nervous system.
Sources Of Water Pollution: -
1. Sewage and domestic waste- Sewage contains minerals and organic matter,
human excreta, soap, detergent, garden waste, and metals. Sewage contains
a trace quantity of toxic metals such as Cu, Cr, Zn, Mn, Pb, and Ni. It also
contains decomposable organic matter and it exerts O2 demand. Organic
matter includes fatty acids, esters, amino acids, amides, amino sugars and
proteinaceous amine.
2. Industrial Effluents- In this category, we have toxic chemicals, hazardous
compounds, phenols, aldehydes, ketones, amines, cyanides, metallic waste,
acids, alkalis, oil, grease, suspended solid dyes, non-biodegradable matter,
radioactive waste and thermal pollutants.
3. Agricultural Discharge- Plant nutrients, pesticides, insecticides,
herbicides, farm waste, manure slurry sediments, plants and animals debris
and drainage from soil erosion.
4. Fertilizers- (main components of fertilizers are N, K, and P)
Fertilizers increase the total crop yield but at the expense of protein loss. The
balance of amino acids within the protein is disrupted, super-phosphates lead
to Fe, Cu, and Zn deficiency in plants, and potash treatment decreases
valuable nutrients like ascorbic acid and carotene in fruits and vegetables.
Clear water bodies are known as oligotrophic. When clear water bodies are
converted into marshy land by excessive algal bloom which is promoted due
to N, P, and K fertilizers and are washed into water bodies, this phenomenon
is known as eutrophication.
5. Detergents- Detergents contain surface active agents and contribute
phosphates of sodium silicates, sodium sulphates, and amides. They are
responsible for foaming. We have surfactants like alkyl benzyl sulphonates
(ABS) that persist for a longer time so they have been replaced by linear
alkyl benzyl sulphonates (LABS) which can be degraded.
6. Toxic Metals- Heavy metals such as Hg, Cd, Pb, As, Co, Mn, Fe, and Cr are
very harmful to aquatic ecosystems. They are added from industrial
processes, domestic sewage discharge, land runoff and fossil fuel burning.
7. Silt- These are soil particles which are the most damaging pollutants in hill-
streams. They create high turbidity in water and hinder the free movement
of aquatic organisms and, growth and productivity of fishes. They may also
lead to flood as the deposition of slits increases the water level.
8. Thermal Pollutants- These are due to atomic, nuclear and thermal power
plant waste, and discharge of unutilized heat in water bodies.
9. Radioactive Pollutants- These include fission and fusion products. Radio-
nuclei are added from nuclear power plants, nuclear reactors, nuclear tests,
nuclear installations or medical waste. They have a very long lifetime, so
they cause various diseases like genetic aberration, cancer etc.
Chemical Speciation:
The term chemical speciation means the identification of inorganic,
organic or organometallic species of an element/chemical present in the
environment. It is important to identify such species. The biological
activity e.g., the toxicity of an element may vary widely depending on the
species. The physical properties (volatility, solubility, etc.) and chemical
behaviour differ among the different species of an element. They affect the
mobility or transportation of the element concerned in the environment and
its toxicity to man and other organisms. These species can be identified and
quantified by various analytical methods.
Lead (Pb):
The possible species of Pb in water may be classified according to size.
The soluble portion passing through a 0.45μm membrane filtered may be
associated with colloidal particulate material.
In freshwater at pH 6, Pb occurs in the form of inorganic non-colloidal,
non-labile species and the composition is Pb2(OH)2CO3. At the higher pH
values of most surface water, Pb is more likely to be associated with
colloidal matter. In seawater, Pb is generally present as colloidal inorganic
matter. The species which have been identified as Pb in aqueous media are
Pb(CH3)4 and Pb(CH3)3+, Pb(CH3)22+, PbSO4, Pb3O4, PbO, and PbS. They
reach water bodies through street dents. The other species of lead are
(CH3)3C2H5Pb, (CH3)2(C2H5)2Pb, (CH3)(C2H5)Pb, (C2H5)4Pb.
Pb(CH3)4 → (CH3)3Pb+ → (CH3)2Pb2+ → CH3Pb3+
Air borne Pb compounds are found in both gaseous and particulate
matter. X-ray powder diffraction confirms the presence of PbSO4,
(NH4)2SO4, Pb3O4, PbO, PbSO4, etc. in street dust and reported to be
PbSO4(NH4)2SO2, PbBrCl22NH4Cl, PbBrCl(NH4)2BrCl etc.
Fig. Pathways of Pb in the environment
As mentioned above the atmosphere over Los Angeles alone has input of
about 20 tonnes of Pb daily. Greenland ice and Southern California basin
sediment have shown appreciable Pb content. The organo-lead compounds
are more toxic than inorganic lead. Commercially, five tetraalkyl lead
(TAL) compounds are important: tetramethyl lead (TML),
tetramethylethyl lead (TMEL), dimethyldiethyl lead (DMDEL),
methyltriethyl lead (MTEL) and tetraethyl lead (TEL). Most organic Pb
enters the atmosphere during manufacture, transfer of leaded gasoline and
use in vehicles.
Mercury (Hg):
Interest in chemical speciation virtually originated from the incident of
Mercury poisoning, starting with the Minamata episode (1953). Extensive
research has been carried out since the late 1950s on the aquatic chemistry
of Hg, its biotransformation, toxicity to biota and monitoring and analysis
techniques. It has been established that there is a remarkable difference in
toxicity between methyl mercury compound (CH3Hg)+, (CH3)2Hg and
other species, viz. Hg0, Hg2+, etc. These methyl mercury compounds are
villains in all fatal incidents due to Hg. Hence, the estimation of methyl
mercury compounds, particularly in biological material, is of considerable
importance. The major analytical approach in speciation has been to
distinguish between. Hg0, Hg2+, CH3Hg and (CH3)2Hg. A summary of the
environmental chemistry of Hg is given below-
Organic compounds (alkyl) of Hg have attained notoriety for their toxic
effect. Their presence in waterbodies requires constant monitoring. The
permissible limit of Hg in drinking water is 2 ppb. The best and most
convenient method is the Flameless Atomic Absorption Method, while the
dithizone method may also be used as it is fairly selective for Hg.
Arsenic (As):
Methyl arsenic compounds are found in several water bodies. Air contains
Arsenic mostly as an inorganic species. Some trimethyl arsenic in vapour
form can also be found and some methyl arsenic compounds as
particulates. Arsenic analysis is generally carried out by the silver
diethyldithiocarbonate spectrophotometrically.
Arsenic speciation in air samples is carried out using a glass wool filter to
trap the particulates, followed by silvered glass beads to trap volatile
arsines. The arsines are removed by dil. NaOH wash and analysed as
above, after NaBH4 reduction. Ambient air appears to contain As mostly
as the inorganic species, some (CH3)3 As in vapour form, and some methyl
arsenic compounds as particulates.
In water, speciation of arsenic (As) has been conducted by iodide (I-)
reduction. As(V) compound converted to iodides in the presence of I-,
which is then allowed to react with diethylammonium diethyl
dithiocarbamate to form arsenic complexes of diethyl dithiocarbamate.
As[(C2H5)2N-CS2]3
CH3-As[(C2H5)2N-CS2]
(CH3)2-As[(C2H5)2N-CS2]
These species can be identified by gas chromatography. Organometallic
and organometalloidal species are identified by liquid chromatography.
Fig: Environmental Chemistry of Arsenic