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Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com
ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79
www.ijera.com 69 | P a g e
Characterization of Wastewater in Rajouri Town, Jammu And
Kashmir, India
Zishan Aslam*, Yawar Mushtaq Raina**, Irfan Mohiuddin***
*(Assistant Professor, Department of Civil Engineering, CoET, BGSB University Rajouri, J & K)
** (Junior Engineer, Public Works (R & B) Department, Government of Jammu & Kashmir, India)
*** (B-Tech Civil engineering, BGSB University Rajouri, J & K)
ABSTRACT
Water exaggerated physically, chemically as well as biologically is known as wastewater. Thrown away process
of solid waste and its treatment has been the foremost environmental setback for most of the cities in India
especially in rural area. To make people aware about the level of contaminants in wastewater and to suggest the
ways of treatment of wastewater which will result in disposing off of domestic effluents without any danger to
human health, a study on characteristics of wastewater in Rajouri town in Jammu and Kashmir was conducted.
Concentrations of various physicochemical parameters like Total dissolved solids (TDS), pH, Turbidity,
Biochemical Oxygen Demand (BOD), Chemical Oxygen Demand(COD), Alkalinity, Hardness Chloride
Content, Nitrogen, Ammonium, Phosphorous, Iron and E-coli bacteria were determined. Study was done on five
different sampling locations. All the parameters were found to be generally exceeding the limits set by W.H.O
except for few sampling locations. The sampling site which was found to be the most polluted was Muradpur
(SL 5) thus affecting the population there because of being on the downstream side and the least affected site
was Kheora (SL2). In some sampling stations due to presence of vegetation at the disposal sites, the quality of
sewage to some extent are acceptable may be because the vegetation absorb some of its undesirable constituents.
To treat this wastewater and make it suitable for various purposes like irrigation, vegetation and other domestic
purposes a treatment plant which will benefit population of 37,552 souls. Construction of wetlands will also lead
to effective treatment and management of wastewater.
Keywords: Analysis, Environment, Parameters, Rajouri Treatment, Wastewater.
I. Introduction
Water is one of the most significant natural
resource for survival on earth, almost all the works to
be done depend on water. Water has severally been
exaggerated physically, chemically as well as
biologically known as wastewater. Wastewater
generally signifies the liquid waste. It is released
from familial areas like discharge from toilets,
urinals, stables [1]. The manufacture of waste from
human doings is unavoidable. A momentous fraction
of this waste will end up as wastewater. The other
sources of domestic wastewater includes outflow
from gutter, gangrenous tank emancipation, grey
water (water used for washing of clothes, cooking,
floors etc) and rainwater assembled from roof top or
balconies [2]Wastewater is also discharged from
marketable chattels, factories [1]. Wastewater from
industries and marketable chattels normally consists
of heavy metals, huge amount of organic matter,
nitrate, detergents, inorganic salt, oil etc[3].
Wastewater discharged from groundwater is in
the form of leachate beginning from close by
depositing place and due to careless handling of
landfill sites it gets polluted [4]. It is also known as
municipal wastewater which consists of huge amount
of pollutants as a consequence of jumbling of
wastewater from singular fonts like domestic,
industrial and agricultural [5]. Municipal wastewater
also consists of emancipation urban rainfall overflow
from roads, roofs of car and pavements which consist
of oils and animal faeces [2]. If there is a sewerage
treatment plant in an area then there are also chances
of water getting polluted because of overflow.
Emulsions, agricultural drainage, diffuse also pollutes
water and make it unfit for any use [6].
Population of the country which have increased
at brisk pace have changed the way of living of
people as a result of which municipal solid waste
have also [7]. Total waste generated in India by
metro cities is 9,275 Mld [8]. Among the total
wastewater engendered, only 31% is taken care off
before being disposed off, the rest 69% is never taken
care off. About 70 % of the country is contaminated
due to household and industrial waste [9]. Human
doings have negatively crashed on excellence of
water in the downstream fragments of the major
rivers [10]. As far as rural areas are concerned 95%
of population depends on ground water for household
use [11]. About 80% of water pollution in India is
done by domestic waste [12]. There is less or no
facilities provided for gathering wastewater and to set
out off after management or treatment. In India the
waste whichever is disposed of is disposed off in
RESEARCH ARTICLE OPEN ACCESS
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substandard way [13] which has lead to dangerous
and unhygienic conditions in many parts of the
country. Amount of pollution caused by wastewater
has generally been difficult to judge. Thus Treatment
and secure clearance of wastewater is compulsory.
This will shield the environment and environmental
management making it pollution free because the
wastewater accumulated from cities and towns
should finally revisit to accepting water or may be to
the land. The treatment is of utmost importance
especially in rural areas where people are less
educated. Before the ways of treatment are suggested
it is necessary to carry out the analysis of wastewater
which is done by analyzing physical, chemical and
biological characteristics. Few important are Total
dissolved solids (TDS), pH, Turbidity, Biochemical
Oxygen Demand (BOD), Chemical Oxygen
Demand(COD), Alkalinity, Hardness Chloride
Content, Nitrogen, Ammonium, Phosphorous, Iron
and E-coli bacteria etc [1]. The treated water can be
used for various valuable functions like growing
plants, vegetables and other useful purposes [14]
The main objective of the paper is to study,
characteristics of wastewater in Rajouri town in
Jammu and Kashmir and then compare it with the
standard set by WHO, so that general public could be
made aware about the level of contaminants in
wastewater and to suggest the ways of treatment of
wastewater which will result in disposing off of
domestic effluents without any danger to human
health.
1.1 Study area
Rajouri district situated in the south western
division of Jammu and Kashmir state is famously
known as the land of kings covers an area roughly
equal to 2630 sq km and lies between latitudes
330
00’00”& 330
35’20” North and longitudes
740
08’00” & 740
42’30” East as per survey of India. It
lies at an altitude nearly equal to 915m above Mean
Sea Level (MSL) enclosed by well-known Pir-Panjal
hills. Rajouri town is the chief sector of the Rajouri
district. Population of the town is 37,552 as per
census of 2011. Out of this 57% are males and rests
are females. Rajouri town is situated near the
highway of district Poonch (85km away) and Jammu
about 154 km away and is enclosed by Udhampur
district, Poonch, Jammu district and Mirpur
(Pakistan). The atmosphere in southern division
(Nowshera, Sunderbani and Kalakote) of the
constituency is half humid where as in northern
division (Thannamandi and Koteranka, Darhal) it is
pleasant. In Northern part of the district rainfall is
heavy beside rainfall these areas also experiences
snowfall. Rajouri town also experiences snow fall
occasionally like in Dec 2012. Average variation in
of temperature in area is 7°C to 40°C. The normal
yearly rainfall is 76.9cm. River pouring throughout
Rajouri town make way into the town from Darhal
and Thanamandi. They congregate near Kheora then
make its way through entire town via Madina
Calony, Jawahar Nagar area, Chapriya and Muradpur
finally meeting with another river at Nowshera,
which ultimetly flows into Pakistan.
In Rajouri unacceptable running and no proper
study of the wastes have caused lot of problems to
uneducated people of the area In Rajouri.90-95% of
the waste is plonked in an inappropriate way in open
dumps, which ultimately pollutes the environment.
The sewage of the area is very turbid as people in the
area prefer to discharge faecal matter along with
other wastes in adjoining drain. Fig 1 shows the Map
of Rajouri district.
Figure 1: Map of Rajouri District, Jammu &
Kashmir, India (Source: Maps of India)
II. Materials and Method
1.1. General
Wastewater is generally released from domestic
residences, commercial properties and industries [1].
The study holds more importance in countries like
India especially in rural areas.
1.2. Wastewater Collection and Sampling
All in all five sampling stations were chosen for
characterization viz Jawahar Nagar (SS 1), Kheora
(SS 2), Madina Colony (SS 3), D.C Colony (SS 4),
Muradpur (SS 5). The Stations were chosen for
analysis because they cover the entire town besides
making their way into rivers while moving from
these selected sampling stations. These stations were
densely populated which ultimately helped in
carrying out the research work in a better way and
obtain good results. The samples were mainly of
domestic quality as area lacks industries. The drain
from which samples were collected as a rough
discharge of 1 m3
/s. Samples were collected from
these stations at different timings of the day.
Sampling was done in such a way so that average
values of various characteristics of sewage could be
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ascertained. Two types of sampling were done i.e.
Grab and Composite sampling. Samples were
collected in 1000 ml clean plastic bottles.
The drain has varied discharges at different
periods of day. Sampling was mostly carried out at 9
am in the morning at all the stations. The drain from
which samples were collected was connecting a large
area. The drain of Jawahar Nagar (SS 1), was having
a length of about 600 m upto the point from where
sewage was changing its course into an open area in
the form of swamp, where as drain of Kheora (SS 2),
was the longest about 800m long and that of Medina
colony (SS 3), DC Colony (SS 4) and Muradpur (SS
5), being 400m, 450m and 700m long respectively.
The sewage of all the stations finally finds its way
into a nearby river called Rajouri River without any
pretreatment, thus affecting a large population mainly
on the downstream. The details of five selected
sampling stations are shown in Table 1
Table 1: Details of five sampling stations
Station Name of the Location Length of
drain (m)
SL 1 Jawahar Nagar 600
SL 2 Kheora 800
SL 3 Medina Colony 400
SL 4 DC Colony 450
SL 5 Muradpur 700
2.3 Data Analysis
After collection the samples were Stored at 4°C
in Water Quality Analysis Lab. Tests were carried
out for Total dissolved solids (TDS), pH, Turbidity,
Biochemical Oxygen Demand (BOD), Chemical
Oxygen Demand(COD), Alkalinity, Hardness
Chloride Content, Nitrogen, Ammonium,
Phosphorous, Iron and E-coli bacteria at the selected
stations. Standard Methods for the assessment of
Water and Wastewater by American Public Health
Association [15] were used for carrying out tests. The
results obtained were compared with standards set by
World health organisation [16].
III. Results and Discussions
Details of the parameters of the wastewater
samples compared with the emblematic values of
Domestic wastewater set by W.H.O [16]. The range
of the parameters and average of the parameters at
different sampling locations are shown Table 2. This
table shows that the wastewater is contaminated at
the greater extent in some of the sampling stations.
This is mainly due to poor or hardly any treatment of
wastewater
3.1. Variations of wastewater Parameters
Total dissolved solids (TDS) are amalgamation
of all dead and untreated materials in a wastewater in
dissolved and suspended form. The TDS
amalgamation at sampling station SL5, SL4, SL1,
SL3 was high that is 2000 mg/ltr 1850 mg/ltr 1700
mg/ltr and 1550 mg/ltr respectively shown in figure
2. They all were exceeding the permissible limit at
these stations. At station SL2 it was safe and value
was 1250 mg/ltr. TDS have high values at some
stations due to the fact that waste is disposed off in an
in appropriate way at the site. Towering values of
TDS reduces the succulence and may escort to
gastro-intestinal aggravation in humans [12]. The pH
is quantity of activity of ionized Hydrogen (H+
) ions
in wastewater solution [17]. The pH value of all the
five Sampling locations was found to be lying
between 7.82 and 9.4. The maximum among all was
found at SL5 and SL2 was having the least pH value
followed by SL1 where it was 7.84 as indicated in fig
3. Wastewater was found to be safe for all the four
stations viz SL1, SL2, Sl3 and SL4 but SL5 was
exceeding the permissible limit. So on the whole
wastewater for the town with respect to pH can be
deemed as harmless. The effect of pH on hydrogen
production from glucose from mixed culture was
studied by [18] revealed that multiplicity of germs
increases with increase in pH value. Turbidity is the
measurement of quantity of particulates dangled in
water [19]. It computes the amount of light dispersed
when it is released on dangled solids. Turbidity at
three locations i.e SL1, SL3 and SL5 was exceeding
the limit set by W.H.O [16] where it was 32 NTU, 35
NTU, 42 NTU, where as sampling locations SL 2 and
SL 4 27 NTU and 29 NTU and was safe as shown in
fig 4. On the whole the mean turbidity on whole
Rajouri town 33 NTU clearly exceeding the standard
limit and wastewater in this regard was deemed as
unfit. Turbidity when exceeds its permissible limit
can cause health problems for example water borne
diseases like protozoa [20]. Biochemical oxygen
demand (BOD) is the extent of disbanded oxygen
obligatory for aerobic heritable living things in water
to shatter behind alive material there in a given water
sample at unambiguous warmth in a distinct eon of
time. BOD5 at all the sampling locations was
exceeding the permissible limit set by W.H.O [16]
for discharged domestic wastewater. At different
locations Maximum BOD5 was 142mg/ltr at SL1
with minimum being 95 mg/ltr at SL2. At SL3, SL4,
SL5 BOD5 was 107 mg/ltr, 97 mg/ltr and 123 mg/ltr
respectively as indicated in figure 5. Overall
wastewater was unsafe with respect to BOD5. COD is
value of oxygen analogous to the crude matter of the
water defenseless to rust due to husky compound
oxidant and hence it is important to unrefined toxic
waste [21]. The COD of all five selected samples
were in between 15.8 mg/ltr to 57.5mg/ l, with
sampling station SL5 having the limit intensity of
COD i.e 57.8. These levels of COD show the
subsistence of unrefined pollutants in water. Fig 6
shows the intensity of COD at all the sampling
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locations. Attendance of COD can be exploited as
unrefined indicators to review the wastewater toxic
waste.
Appraise of ability of water to deactivate acids is
known as alkalinity. If water is too alkaline
obnoxious taste is there in water. The alkalinity at the
sampling locations was varying between 11.5 mg/ltr
and 15.5 mg/ltr with maximum at SL 3 and minimum
at SL 2 shown in fig 7. Alkalinity at other locations
SL 1, SL 4, SL 5 was 12 mg/ltr, 18 mg/ltr and 14
mg/ltr. There is no limit set for alkalinity for
wastewater by W.H.O [16]. Alkaline water is still
considered to be harmful for human health. Working
out of the figure of divalent ions which mainly
icludes calcium and magnesium in attendance there
in water is known as Hardness [22]. Hardness of
water at study area was varying in between 104
mg/ltr to 147 mg/ltr in phrase of CaCO3 (fig 8) at SL
2 and SL 5 . At other stations the variation of
hardness was 118 mg/ltr at SL1 to 125 mg/ltr at SL 3
and then 127 mg/ltr at SL 4. There is no limit for
hardness for discharged domestic wastewater as it
can be used for any purpose safely except for
drinking because excessive calcium and magnesium
cause’s stones in kidney and laxative problems
respectively but the shortage of these constituents
may lead to utilitarian modifications. Chloride (Cl -
)
is an element that crop up in nature and is established
in plenty. Chloride content at the sampling locations
was in the range of 382 mg/ltr to 697.62 mg/ltr with
maximum at sampling location SL 2 and minimum at
SL5 as shown in fig 9. At other locations SL 1, SL 3
and SL4, the chloride content was 469.21 mg/ltr,
586.86 mg/ltr, 593.23 mg/ltr respectively. Chloride
absence is providentially less, if not looked after and
treated well can cause death but if it is in excess it
may lead to health risks to people going through
heart related diseases and kidney sickness [12].
Nitrogen is in attendance in sewage in the shape of as
unrefined compounds (proteins amines, amino acids
and urea) and ammonium salts as in organic
compound. Nitrogen at the sampling locations was
varying between 25.9 mg/ltr to 51.3 mg/ltr with least
at SL 1 and maximum at SL 5. At SL 2, SL3, SL 4, it
was 27.8 mg/ltr, 37.4 mg/ltr, 44.5 mg/ltr respectively.
It is important for both plants and animals but the
excessive nitrogen is detrimental to the both [12].
Nitrogen was exceeding the permissible limit as SL 5
on all other locations it was within the permissible
limit (fig 10). Ammonia is the multifaceted by
hydrogen and nitrogen (NH3) gas and is clutched to
wastewater due rotting nitrogenous untreated matter.
Amount of nitrogen determines the age of sewage
[1]. Ammonia at the sampling locations was varying
between 2.3 mg/ltr to 5.7 mg/ltr (fig 11) with least at
SL 2 and maximum at SL 5. At SL 1, SL3, SL 4, it
was 2.7 mg/ltr, 3.5 mg/ltr, 4.4 mg/ltr respectively.
Lesser quantity ammonia is mordant; on the other
hand if its value is increased it is dangerous to
animals living in water and dialysis patients [12].
Ammonia at SL5 was exceeding the permissible
limit. Food scums supplies phosphorous to domestic
wastewater. Using enhanced amount of artificial
detergents add significantly to percentage of
phosphorous in sewage. Phosphorous at the sampling
locations was varying between 5.5 mg/ltr to 9.6
mg/ltr (fig 12) with least at SL 3and maximum at SL
5. At SL 1, SL 2, SL 4, it was 7.85 mg/ltr, 6.4 mg/ltr,
8.8 mg/ltr respectively. Phosphorous at all the
locations was exceeding the limit prescribed by
W.H.O [16].
Iron is normally found in water as ferrous or
ferric structure. It is not dangerous to wellbeing yet it
is considered for the visual intentions. Existence of
iron alters the color of water [23]. Iron at the
sampling locations was varying between 1.4 mg/ltr to
4.4 mg/ltr (fig 13) with least at SL 2 and maximum at
SL 1. At SL 3, SL 4, SL 5, it was 3.6 mg/ltr, 3.2
mg/ltr, 3.7 mg/ltr respectively. Except for SL2 all the
locations were exceeding the permissible limit. Since
this wastewater is having excess iron content it won’t
be suitable to use it for irrigation purposes. E-coli are
the dowel figured aerobic bacteria originates in the
intestinal territory of man, they are not destructive to
man and are constructive in demolishing untreated
material in biological treatment process. E-coli was
ranging in between 2.5 -3.7 MPN/100 ml (fig 14).
However due to presence of vegetation at the
disposal sites, the quality of sewage at some stations
to some extent are acceptable as the vegetation
absorb some of its undesirable constituents.
Table 2: Physico-chemical parameter’s estimation of Waste water at Rajouri Town
Parameter Range Mean
Value
Typical Value of Untreated Domestic wastewater
Weak Medium Strong
Total Dissloved Solids (mg/l) 1250-2000 1670 250 500 850
pH 7.82-9.4 8.37 5-9
Turbidity (NTU) 32-42 33 - - -
BOD5 (mg/l) 95-142 112.8 110 220 400
COD (mg/l) 15.8-57.5 36.92 250 500 100
Alkalinity as Caco3 (mg/l) 11.5-15.5 14.2 50 100 200
Chloride (mg/l) 382-697.6 545.81 30 50 100
Hardness (mg/l) 104-147 124.2 - - -
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Nitrogen (mg/l) 25.9-51.3 37.38 20 40 85
Ammonia (mg/l) 2.3-5.7 3.72 12 25 50
Phosporous (mg/l) 5.5-9.6 7.63 4 8 15
Iron (mg/l) 1.4-4.4 3.26 - - -
E-Coli (Nos/100mg) 2.5-3.7 3.17 - - -
Typical values of untreated wastewater (source: Metcalf and eddy, Inc, 5-36)
Fig. 2: showing values of Total Dissolved Solids at different sampling locations
Fig. 3: showing values of pH at different sampling locations
Fig. 4: showing values of Turbidity at different sampling locations
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Fig. 5: showing values of BOD5 at different sampling locations
Fig. 6: showing values of COD at different sampling locations
Fig. 7: showing values of Alkalinity at different sampling locations
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Fig. 8: showing values of Chloride Content at different sampling locations
Fig.9: showing values of Hardness at different sampling locations
Fig.10: showing values of Nitrogen at different sampling locations
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Fig.11: showing values of Ammonia at different sampling locations
Figure 12: Showing values of Phosphorous at the sampling station
Fig.13: showing values of Iron Content (Fe) at different sampling locations
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Fig.14: showing values of No. of Coliform bacteria’s at different sampling locations
3.2. Suggested measures for treatment of
Wastewater
The wastewater analyzed was found to be
polluted in some of the sampling locations so in
order to supply pure water to general public and use
this wastewater for useful purposes like irrigation,
agricultural and other domestic purposes which
includes bathing, washing, cooking etc. The
wastewater should be treated well before it is
supplied. Here some of the parameters of wastewater
were exceeding the limits set by W.H.O [16]. These
parameters includes TDS, pH, Turbidity, BOD5,
Nitrogen, ammonia, phosphorous and Iron. Some of
the suggested measures to reduce their
concentrations and their treatment are discussed as
under
Total Dissolved Solids: Total dissolved solids
cannot be removed by unadventurous treatment
methods. Accumulation of chemicals enhances the
intensity of TDS [24]. Zeolite process and softening
may just lessen TDS to some extent [25]. To reduce
the amount of TDS entirely processes like Reverse
osmosis and electro dialysis may be used which will
be cost-effective as well [26]
pH: Wastewater having soaring pH may be allowed
to scamper in the course of a tank where citric or
acetic acid may be added to lessen the pH. Filters,
water softeners and tanks should be washed out and
redeveloped occasionally. If the water is to be
exercised for irrigation, crops or drinking, salinity
should be checked using a hydrometer.
Turbidity: Its treatment may be done either by
settling or filtration. Quantity of chemical reagents
depends upon the application and they should be
dosed into the wastewater stream to enhance the
usefulness of the settling and filtration. Municipal
wastewater plants frequently eliminate turbidity by
amalgamation of sand filtration, settling tanks and
clarifiers
BOD: It should be removed by constructing the
treatment plant such as stabilizing pond which
reduces the BOD in the wastewater released to
rivers. Wastewater treatment plants are intended for
utility as bacteria ranch, where bacteria are provided
with oxygen and untreated waste. The surplus
bacteria developed are eradicated as mud, and the
solid waste is then arranged of on land
Nitrogen: It can be eliminated from drinking water
by distillation, reverse osmosis, and ion exchange.
Among this reverse osmosis is the best and cost
effective. In this method force is pertained to water
to move it in the course of a half-porous film. When
this happens more than half of the impurities are
wiped out. About 85 to 95 percent of the nitrogen
can be confiscated with reverse osmosis.
Ammonia: High ammonia can be removed by
chlorination and breakpoint chlorination [27].
Phosphorous: High Phosphorous content can be
diminished by use of alum
Iron: Treatment of Iron may be done using
sequestering, exchange of ions, oxidation filtration
and settling. Amount of iron present in water will
signify the method which will be best suited.
Beside the above discussed processes
construction of wetlands will also lead to effective
treatment and management of wastewater.
IV. Conclusion
After carrying out the analysis of wastewater the
mean values of the parameters viz Total dissolved
solids (TDS), pH, Turbidity, Biochemical Oxygen
Demand (BOD), Chemical Oxygen Demand(COD),
Alkalinity, Hardness, Chloride Content, Nitrogen,
Ammonium, Phosphorous, Iron and E-coli were
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found to be 1670 mg/ltr, 8.37, 33 NTU, 112.8, 36.92
mg/ltr, 14.2 mg/ltr, 545.81 mg/ltr, 124.2 mg/ltr,
37.38 mg/ltr,3.72 mg/ltr,7.63 mg/ltr,3.26 mg/ltr,3.17
MPN/100ml respectively. It was found that among
these parameters TDS, Turbidity, BOD, Nitrogen,
Phosphorous and Iron were increasing the limits set
by WHO. Overall the Rajouri town with respect to
these parameters was found to be unsafe. Among all
the sampling locations that is SL 1 (Jawahar Nagar),
SL 2 (Kheora) SL 3 (Medina Colony) SL 4 (DC
Colony), SL 5 (Muradpur). Among these Locations
the site which was found to be the most polluted was
Muradpur (SL 5) thus affecting the population there
because of being on the downstream side and the
least affected site was Kheora (SL2). In some
sampling stations due to presence of vegetation at
the disposal sites, the quality of sewage to some
extent are acceptable may be because the vegetation
absorb some of its undesirable constituents. Hence a
treatment plant is suggested to treat the wastewater
and then used for various useful purposes like
irrigation, washing, bathing etc which will benefit
population of 37,552 souls. Construction of wetlands
will also lead to effective treatment and management
of wastewater.
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Characterization of Wastewater in Rajouri Town, Jammu And Kashmir, India

  • 1. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 69 | P a g e Characterization of Wastewater in Rajouri Town, Jammu And Kashmir, India Zishan Aslam*, Yawar Mushtaq Raina**, Irfan Mohiuddin*** *(Assistant Professor, Department of Civil Engineering, CoET, BGSB University Rajouri, J & K) ** (Junior Engineer, Public Works (R & B) Department, Government of Jammu & Kashmir, India) *** (B-Tech Civil engineering, BGSB University Rajouri, J & K) ABSTRACT Water exaggerated physically, chemically as well as biologically is known as wastewater. Thrown away process of solid waste and its treatment has been the foremost environmental setback for most of the cities in India especially in rural area. To make people aware about the level of contaminants in wastewater and to suggest the ways of treatment of wastewater which will result in disposing off of domestic effluents without any danger to human health, a study on characteristics of wastewater in Rajouri town in Jammu and Kashmir was conducted. Concentrations of various physicochemical parameters like Total dissolved solids (TDS), pH, Turbidity, Biochemical Oxygen Demand (BOD), Chemical Oxygen Demand(COD), Alkalinity, Hardness Chloride Content, Nitrogen, Ammonium, Phosphorous, Iron and E-coli bacteria were determined. Study was done on five different sampling locations. All the parameters were found to be generally exceeding the limits set by W.H.O except for few sampling locations. The sampling site which was found to be the most polluted was Muradpur (SL 5) thus affecting the population there because of being on the downstream side and the least affected site was Kheora (SL2). In some sampling stations due to presence of vegetation at the disposal sites, the quality of sewage to some extent are acceptable may be because the vegetation absorb some of its undesirable constituents. To treat this wastewater and make it suitable for various purposes like irrigation, vegetation and other domestic purposes a treatment plant which will benefit population of 37,552 souls. Construction of wetlands will also lead to effective treatment and management of wastewater. Keywords: Analysis, Environment, Parameters, Rajouri Treatment, Wastewater. I. Introduction Water is one of the most significant natural resource for survival on earth, almost all the works to be done depend on water. Water has severally been exaggerated physically, chemically as well as biologically known as wastewater. Wastewater generally signifies the liquid waste. It is released from familial areas like discharge from toilets, urinals, stables [1]. The manufacture of waste from human doings is unavoidable. A momentous fraction of this waste will end up as wastewater. The other sources of domestic wastewater includes outflow from gutter, gangrenous tank emancipation, grey water (water used for washing of clothes, cooking, floors etc) and rainwater assembled from roof top or balconies [2]Wastewater is also discharged from marketable chattels, factories [1]. Wastewater from industries and marketable chattels normally consists of heavy metals, huge amount of organic matter, nitrate, detergents, inorganic salt, oil etc[3]. Wastewater discharged from groundwater is in the form of leachate beginning from close by depositing place and due to careless handling of landfill sites it gets polluted [4]. It is also known as municipal wastewater which consists of huge amount of pollutants as a consequence of jumbling of wastewater from singular fonts like domestic, industrial and agricultural [5]. Municipal wastewater also consists of emancipation urban rainfall overflow from roads, roofs of car and pavements which consist of oils and animal faeces [2]. If there is a sewerage treatment plant in an area then there are also chances of water getting polluted because of overflow. Emulsions, agricultural drainage, diffuse also pollutes water and make it unfit for any use [6]. Population of the country which have increased at brisk pace have changed the way of living of people as a result of which municipal solid waste have also [7]. Total waste generated in India by metro cities is 9,275 Mld [8]. Among the total wastewater engendered, only 31% is taken care off before being disposed off, the rest 69% is never taken care off. About 70 % of the country is contaminated due to household and industrial waste [9]. Human doings have negatively crashed on excellence of water in the downstream fragments of the major rivers [10]. As far as rural areas are concerned 95% of population depends on ground water for household use [11]. About 80% of water pollution in India is done by domestic waste [12]. There is less or no facilities provided for gathering wastewater and to set out off after management or treatment. In India the waste whichever is disposed of is disposed off in RESEARCH ARTICLE OPEN ACCESS
  • 2. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 70 | P a g e substandard way [13] which has lead to dangerous and unhygienic conditions in many parts of the country. Amount of pollution caused by wastewater has generally been difficult to judge. Thus Treatment and secure clearance of wastewater is compulsory. This will shield the environment and environmental management making it pollution free because the wastewater accumulated from cities and towns should finally revisit to accepting water or may be to the land. The treatment is of utmost importance especially in rural areas where people are less educated. Before the ways of treatment are suggested it is necessary to carry out the analysis of wastewater which is done by analyzing physical, chemical and biological characteristics. Few important are Total dissolved solids (TDS), pH, Turbidity, Biochemical Oxygen Demand (BOD), Chemical Oxygen Demand(COD), Alkalinity, Hardness Chloride Content, Nitrogen, Ammonium, Phosphorous, Iron and E-coli bacteria etc [1]. The treated water can be used for various valuable functions like growing plants, vegetables and other useful purposes [14] The main objective of the paper is to study, characteristics of wastewater in Rajouri town in Jammu and Kashmir and then compare it with the standard set by WHO, so that general public could be made aware about the level of contaminants in wastewater and to suggest the ways of treatment of wastewater which will result in disposing off of domestic effluents without any danger to human health. 1.1 Study area Rajouri district situated in the south western division of Jammu and Kashmir state is famously known as the land of kings covers an area roughly equal to 2630 sq km and lies between latitudes 330 00’00”& 330 35’20” North and longitudes 740 08’00” & 740 42’30” East as per survey of India. It lies at an altitude nearly equal to 915m above Mean Sea Level (MSL) enclosed by well-known Pir-Panjal hills. Rajouri town is the chief sector of the Rajouri district. Population of the town is 37,552 as per census of 2011. Out of this 57% are males and rests are females. Rajouri town is situated near the highway of district Poonch (85km away) and Jammu about 154 km away and is enclosed by Udhampur district, Poonch, Jammu district and Mirpur (Pakistan). The atmosphere in southern division (Nowshera, Sunderbani and Kalakote) of the constituency is half humid where as in northern division (Thannamandi and Koteranka, Darhal) it is pleasant. In Northern part of the district rainfall is heavy beside rainfall these areas also experiences snowfall. Rajouri town also experiences snow fall occasionally like in Dec 2012. Average variation in of temperature in area is 7°C to 40°C. The normal yearly rainfall is 76.9cm. River pouring throughout Rajouri town make way into the town from Darhal and Thanamandi. They congregate near Kheora then make its way through entire town via Madina Calony, Jawahar Nagar area, Chapriya and Muradpur finally meeting with another river at Nowshera, which ultimetly flows into Pakistan. In Rajouri unacceptable running and no proper study of the wastes have caused lot of problems to uneducated people of the area In Rajouri.90-95% of the waste is plonked in an inappropriate way in open dumps, which ultimately pollutes the environment. The sewage of the area is very turbid as people in the area prefer to discharge faecal matter along with other wastes in adjoining drain. Fig 1 shows the Map of Rajouri district. Figure 1: Map of Rajouri District, Jammu & Kashmir, India (Source: Maps of India) II. Materials and Method 1.1. General Wastewater is generally released from domestic residences, commercial properties and industries [1]. The study holds more importance in countries like India especially in rural areas. 1.2. Wastewater Collection and Sampling All in all five sampling stations were chosen for characterization viz Jawahar Nagar (SS 1), Kheora (SS 2), Madina Colony (SS 3), D.C Colony (SS 4), Muradpur (SS 5). The Stations were chosen for analysis because they cover the entire town besides making their way into rivers while moving from these selected sampling stations. These stations were densely populated which ultimately helped in carrying out the research work in a better way and obtain good results. The samples were mainly of domestic quality as area lacks industries. The drain from which samples were collected as a rough discharge of 1 m3 /s. Samples were collected from these stations at different timings of the day. Sampling was done in such a way so that average values of various characteristics of sewage could be
  • 3. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 71 | P a g e ascertained. Two types of sampling were done i.e. Grab and Composite sampling. Samples were collected in 1000 ml clean plastic bottles. The drain has varied discharges at different periods of day. Sampling was mostly carried out at 9 am in the morning at all the stations. The drain from which samples were collected was connecting a large area. The drain of Jawahar Nagar (SS 1), was having a length of about 600 m upto the point from where sewage was changing its course into an open area in the form of swamp, where as drain of Kheora (SS 2), was the longest about 800m long and that of Medina colony (SS 3), DC Colony (SS 4) and Muradpur (SS 5), being 400m, 450m and 700m long respectively. The sewage of all the stations finally finds its way into a nearby river called Rajouri River without any pretreatment, thus affecting a large population mainly on the downstream. The details of five selected sampling stations are shown in Table 1 Table 1: Details of five sampling stations Station Name of the Location Length of drain (m) SL 1 Jawahar Nagar 600 SL 2 Kheora 800 SL 3 Medina Colony 400 SL 4 DC Colony 450 SL 5 Muradpur 700 2.3 Data Analysis After collection the samples were Stored at 4°C in Water Quality Analysis Lab. Tests were carried out for Total dissolved solids (TDS), pH, Turbidity, Biochemical Oxygen Demand (BOD), Chemical Oxygen Demand(COD), Alkalinity, Hardness Chloride Content, Nitrogen, Ammonium, Phosphorous, Iron and E-coli bacteria at the selected stations. Standard Methods for the assessment of Water and Wastewater by American Public Health Association [15] were used for carrying out tests. The results obtained were compared with standards set by World health organisation [16]. III. Results and Discussions Details of the parameters of the wastewater samples compared with the emblematic values of Domestic wastewater set by W.H.O [16]. The range of the parameters and average of the parameters at different sampling locations are shown Table 2. This table shows that the wastewater is contaminated at the greater extent in some of the sampling stations. This is mainly due to poor or hardly any treatment of wastewater 3.1. Variations of wastewater Parameters Total dissolved solids (TDS) are amalgamation of all dead and untreated materials in a wastewater in dissolved and suspended form. The TDS amalgamation at sampling station SL5, SL4, SL1, SL3 was high that is 2000 mg/ltr 1850 mg/ltr 1700 mg/ltr and 1550 mg/ltr respectively shown in figure 2. They all were exceeding the permissible limit at these stations. At station SL2 it was safe and value was 1250 mg/ltr. TDS have high values at some stations due to the fact that waste is disposed off in an in appropriate way at the site. Towering values of TDS reduces the succulence and may escort to gastro-intestinal aggravation in humans [12]. The pH is quantity of activity of ionized Hydrogen (H+ ) ions in wastewater solution [17]. The pH value of all the five Sampling locations was found to be lying between 7.82 and 9.4. The maximum among all was found at SL5 and SL2 was having the least pH value followed by SL1 where it was 7.84 as indicated in fig 3. Wastewater was found to be safe for all the four stations viz SL1, SL2, Sl3 and SL4 but SL5 was exceeding the permissible limit. So on the whole wastewater for the town with respect to pH can be deemed as harmless. The effect of pH on hydrogen production from glucose from mixed culture was studied by [18] revealed that multiplicity of germs increases with increase in pH value. Turbidity is the measurement of quantity of particulates dangled in water [19]. It computes the amount of light dispersed when it is released on dangled solids. Turbidity at three locations i.e SL1, SL3 and SL5 was exceeding the limit set by W.H.O [16] where it was 32 NTU, 35 NTU, 42 NTU, where as sampling locations SL 2 and SL 4 27 NTU and 29 NTU and was safe as shown in fig 4. On the whole the mean turbidity on whole Rajouri town 33 NTU clearly exceeding the standard limit and wastewater in this regard was deemed as unfit. Turbidity when exceeds its permissible limit can cause health problems for example water borne diseases like protozoa [20]. Biochemical oxygen demand (BOD) is the extent of disbanded oxygen obligatory for aerobic heritable living things in water to shatter behind alive material there in a given water sample at unambiguous warmth in a distinct eon of time. BOD5 at all the sampling locations was exceeding the permissible limit set by W.H.O [16] for discharged domestic wastewater. At different locations Maximum BOD5 was 142mg/ltr at SL1 with minimum being 95 mg/ltr at SL2. At SL3, SL4, SL5 BOD5 was 107 mg/ltr, 97 mg/ltr and 123 mg/ltr respectively as indicated in figure 5. Overall wastewater was unsafe with respect to BOD5. COD is value of oxygen analogous to the crude matter of the water defenseless to rust due to husky compound oxidant and hence it is important to unrefined toxic waste [21]. The COD of all five selected samples were in between 15.8 mg/ltr to 57.5mg/ l, with sampling station SL5 having the limit intensity of COD i.e 57.8. These levels of COD show the subsistence of unrefined pollutants in water. Fig 6 shows the intensity of COD at all the sampling
  • 4. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 72 | P a g e locations. Attendance of COD can be exploited as unrefined indicators to review the wastewater toxic waste. Appraise of ability of water to deactivate acids is known as alkalinity. If water is too alkaline obnoxious taste is there in water. The alkalinity at the sampling locations was varying between 11.5 mg/ltr and 15.5 mg/ltr with maximum at SL 3 and minimum at SL 2 shown in fig 7. Alkalinity at other locations SL 1, SL 4, SL 5 was 12 mg/ltr, 18 mg/ltr and 14 mg/ltr. There is no limit set for alkalinity for wastewater by W.H.O [16]. Alkaline water is still considered to be harmful for human health. Working out of the figure of divalent ions which mainly icludes calcium and magnesium in attendance there in water is known as Hardness [22]. Hardness of water at study area was varying in between 104 mg/ltr to 147 mg/ltr in phrase of CaCO3 (fig 8) at SL 2 and SL 5 . At other stations the variation of hardness was 118 mg/ltr at SL1 to 125 mg/ltr at SL 3 and then 127 mg/ltr at SL 4. There is no limit for hardness for discharged domestic wastewater as it can be used for any purpose safely except for drinking because excessive calcium and magnesium cause’s stones in kidney and laxative problems respectively but the shortage of these constituents may lead to utilitarian modifications. Chloride (Cl - ) is an element that crop up in nature and is established in plenty. Chloride content at the sampling locations was in the range of 382 mg/ltr to 697.62 mg/ltr with maximum at sampling location SL 2 and minimum at SL5 as shown in fig 9. At other locations SL 1, SL 3 and SL4, the chloride content was 469.21 mg/ltr, 586.86 mg/ltr, 593.23 mg/ltr respectively. Chloride absence is providentially less, if not looked after and treated well can cause death but if it is in excess it may lead to health risks to people going through heart related diseases and kidney sickness [12]. Nitrogen is in attendance in sewage in the shape of as unrefined compounds (proteins amines, amino acids and urea) and ammonium salts as in organic compound. Nitrogen at the sampling locations was varying between 25.9 mg/ltr to 51.3 mg/ltr with least at SL 1 and maximum at SL 5. At SL 2, SL3, SL 4, it was 27.8 mg/ltr, 37.4 mg/ltr, 44.5 mg/ltr respectively. It is important for both plants and animals but the excessive nitrogen is detrimental to the both [12]. Nitrogen was exceeding the permissible limit as SL 5 on all other locations it was within the permissible limit (fig 10). Ammonia is the multifaceted by hydrogen and nitrogen (NH3) gas and is clutched to wastewater due rotting nitrogenous untreated matter. Amount of nitrogen determines the age of sewage [1]. Ammonia at the sampling locations was varying between 2.3 mg/ltr to 5.7 mg/ltr (fig 11) with least at SL 2 and maximum at SL 5. At SL 1, SL3, SL 4, it was 2.7 mg/ltr, 3.5 mg/ltr, 4.4 mg/ltr respectively. Lesser quantity ammonia is mordant; on the other hand if its value is increased it is dangerous to animals living in water and dialysis patients [12]. Ammonia at SL5 was exceeding the permissible limit. Food scums supplies phosphorous to domestic wastewater. Using enhanced amount of artificial detergents add significantly to percentage of phosphorous in sewage. Phosphorous at the sampling locations was varying between 5.5 mg/ltr to 9.6 mg/ltr (fig 12) with least at SL 3and maximum at SL 5. At SL 1, SL 2, SL 4, it was 7.85 mg/ltr, 6.4 mg/ltr, 8.8 mg/ltr respectively. Phosphorous at all the locations was exceeding the limit prescribed by W.H.O [16]. Iron is normally found in water as ferrous or ferric structure. It is not dangerous to wellbeing yet it is considered for the visual intentions. Existence of iron alters the color of water [23]. Iron at the sampling locations was varying between 1.4 mg/ltr to 4.4 mg/ltr (fig 13) with least at SL 2 and maximum at SL 1. At SL 3, SL 4, SL 5, it was 3.6 mg/ltr, 3.2 mg/ltr, 3.7 mg/ltr respectively. Except for SL2 all the locations were exceeding the permissible limit. Since this wastewater is having excess iron content it won’t be suitable to use it for irrigation purposes. E-coli are the dowel figured aerobic bacteria originates in the intestinal territory of man, they are not destructive to man and are constructive in demolishing untreated material in biological treatment process. E-coli was ranging in between 2.5 -3.7 MPN/100 ml (fig 14). However due to presence of vegetation at the disposal sites, the quality of sewage at some stations to some extent are acceptable as the vegetation absorb some of its undesirable constituents. Table 2: Physico-chemical parameter’s estimation of Waste water at Rajouri Town Parameter Range Mean Value Typical Value of Untreated Domestic wastewater Weak Medium Strong Total Dissloved Solids (mg/l) 1250-2000 1670 250 500 850 pH 7.82-9.4 8.37 5-9 Turbidity (NTU) 32-42 33 - - - BOD5 (mg/l) 95-142 112.8 110 220 400 COD (mg/l) 15.8-57.5 36.92 250 500 100 Alkalinity as Caco3 (mg/l) 11.5-15.5 14.2 50 100 200 Chloride (mg/l) 382-697.6 545.81 30 50 100 Hardness (mg/l) 104-147 124.2 - - -
  • 5. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 73 | P a g e Nitrogen (mg/l) 25.9-51.3 37.38 20 40 85 Ammonia (mg/l) 2.3-5.7 3.72 12 25 50 Phosporous (mg/l) 5.5-9.6 7.63 4 8 15 Iron (mg/l) 1.4-4.4 3.26 - - - E-Coli (Nos/100mg) 2.5-3.7 3.17 - - - Typical values of untreated wastewater (source: Metcalf and eddy, Inc, 5-36) Fig. 2: showing values of Total Dissolved Solids at different sampling locations Fig. 3: showing values of pH at different sampling locations Fig. 4: showing values of Turbidity at different sampling locations
  • 6. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 74 | P a g e Fig. 5: showing values of BOD5 at different sampling locations Fig. 6: showing values of COD at different sampling locations Fig. 7: showing values of Alkalinity at different sampling locations
  • 7. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 75 | P a g e Fig. 8: showing values of Chloride Content at different sampling locations Fig.9: showing values of Hardness at different sampling locations Fig.10: showing values of Nitrogen at different sampling locations
  • 8. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 76 | P a g e Fig.11: showing values of Ammonia at different sampling locations Figure 12: Showing values of Phosphorous at the sampling station Fig.13: showing values of Iron Content (Fe) at different sampling locations
  • 9. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 77 | P a g e Fig.14: showing values of No. of Coliform bacteria’s at different sampling locations 3.2. Suggested measures for treatment of Wastewater The wastewater analyzed was found to be polluted in some of the sampling locations so in order to supply pure water to general public and use this wastewater for useful purposes like irrigation, agricultural and other domestic purposes which includes bathing, washing, cooking etc. The wastewater should be treated well before it is supplied. Here some of the parameters of wastewater were exceeding the limits set by W.H.O [16]. These parameters includes TDS, pH, Turbidity, BOD5, Nitrogen, ammonia, phosphorous and Iron. Some of the suggested measures to reduce their concentrations and their treatment are discussed as under Total Dissolved Solids: Total dissolved solids cannot be removed by unadventurous treatment methods. Accumulation of chemicals enhances the intensity of TDS [24]. Zeolite process and softening may just lessen TDS to some extent [25]. To reduce the amount of TDS entirely processes like Reverse osmosis and electro dialysis may be used which will be cost-effective as well [26] pH: Wastewater having soaring pH may be allowed to scamper in the course of a tank where citric or acetic acid may be added to lessen the pH. Filters, water softeners and tanks should be washed out and redeveloped occasionally. If the water is to be exercised for irrigation, crops or drinking, salinity should be checked using a hydrometer. Turbidity: Its treatment may be done either by settling or filtration. Quantity of chemical reagents depends upon the application and they should be dosed into the wastewater stream to enhance the usefulness of the settling and filtration. Municipal wastewater plants frequently eliminate turbidity by amalgamation of sand filtration, settling tanks and clarifiers BOD: It should be removed by constructing the treatment plant such as stabilizing pond which reduces the BOD in the wastewater released to rivers. Wastewater treatment plants are intended for utility as bacteria ranch, where bacteria are provided with oxygen and untreated waste. The surplus bacteria developed are eradicated as mud, and the solid waste is then arranged of on land Nitrogen: It can be eliminated from drinking water by distillation, reverse osmosis, and ion exchange. Among this reverse osmosis is the best and cost effective. In this method force is pertained to water to move it in the course of a half-porous film. When this happens more than half of the impurities are wiped out. About 85 to 95 percent of the nitrogen can be confiscated with reverse osmosis. Ammonia: High ammonia can be removed by chlorination and breakpoint chlorination [27]. Phosphorous: High Phosphorous content can be diminished by use of alum Iron: Treatment of Iron may be done using sequestering, exchange of ions, oxidation filtration and settling. Amount of iron present in water will signify the method which will be best suited. Beside the above discussed processes construction of wetlands will also lead to effective treatment and management of wastewater. IV. Conclusion After carrying out the analysis of wastewater the mean values of the parameters viz Total dissolved solids (TDS), pH, Turbidity, Biochemical Oxygen Demand (BOD), Chemical Oxygen Demand(COD), Alkalinity, Hardness, Chloride Content, Nitrogen, Ammonium, Phosphorous, Iron and E-coli were
  • 10. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 78 | P a g e found to be 1670 mg/ltr, 8.37, 33 NTU, 112.8, 36.92 mg/ltr, 14.2 mg/ltr, 545.81 mg/ltr, 124.2 mg/ltr, 37.38 mg/ltr,3.72 mg/ltr,7.63 mg/ltr,3.26 mg/ltr,3.17 MPN/100ml respectively. It was found that among these parameters TDS, Turbidity, BOD, Nitrogen, Phosphorous and Iron were increasing the limits set by WHO. Overall the Rajouri town with respect to these parameters was found to be unsafe. Among all the sampling locations that is SL 1 (Jawahar Nagar), SL 2 (Kheora) SL 3 (Medina Colony) SL 4 (DC Colony), SL 5 (Muradpur). Among these Locations the site which was found to be the most polluted was Muradpur (SL 5) thus affecting the population there because of being on the downstream side and the least affected site was Kheora (SL2). In some sampling stations due to presence of vegetation at the disposal sites, the quality of sewage to some extent are acceptable may be because the vegetation absorb some of its undesirable constituents. Hence a treatment plant is suggested to treat the wastewater and then used for various useful purposes like irrigation, washing, bathing etc which will benefit population of 37,552 souls. Construction of wetlands will also lead to effective treatment and management of wastewater. References [1] Modi, P.N (2008), Sewage Treatment & Disposal and Waste Water Engineering, 2nd edition.,Standard Book House 1705-A, Nai Sarak, Delhi-6. [2] Husain.A., Ashhar. M. M., & Javed. I (2014): Analysis of industrial wastewater in Aligarh city. Journal of Chemical and Pharmaceutical Research, 6(1):614-621. [3] Rathore, D.S., Rai, N., and Ashiya, P., (2014). Physico Chemical Analysis of Water of Ayad River at Udaipur, Rajasthan (India). International Journal of Innovative Research in Science, Engineering and Technology, 3(4), 11660- 11667. [4] Nagarajan. R, Thirumalaisamy. S & Lakshumanan. E (2012): Impact of leachate on ground water pollution due to non- engineered municipal solid waste landfill sites of erode city, Tamil Nadu, India. Iranian Journal of Environmental Health Sciences & Engineering 9:35. [5] Gulp R.L., Gulp G. L (1971), Advanced Waste-water Treatment, Van No strand Reinhold Company, New York. [6] Roa M. N., Datta A. K. (1987), Wastewater Treatment, 2nd ed., oxford & IBH, New Delhi. [7] Dhere, A.M., Pawar, C.B., Pardeshi, P.B. and Patil, D.A. (2008). Municipal solid waste disposal in Pune city- An analysis of air and groundwater pollution. Current Science, 95(6): 774-777 [8] Bhawan, P., & Nagar, E. A. (2008). Central Pollution Control Board [9] Sangu, R. P. S., and Sharma, S. K., (1987).An assessment of water quality of river Ganga at Garmukeshwar. Ind. J.Ecol., 14(20), 278-287 [10] Chang, H., (2008). Spatial analysis of water quality trends in the Han River basin, South Korea. Water Research, 42 (13):3285 3304 [11] Moharir, A., Ramteke, D.S., Moghe, C.A., Wate, S.R. and Sarin, R.,(2002). Surface and ground water quality assessment in Bina region. Ind. J. Environ.Protec., 22(9): 961-969 [12] World Health Organization (WHO): (1997), Guidelines for Drinking Water Quality, 2nd ed.,Vol. 2 Health criteria and other supporting information, World Health organization, Geneva, pp. 940–949 [13] Chatterjee R (2010): Municipal solid waste management in kohima city-india. Iran J Environ health sci and eng, 7(2):173–180 [14] Raina, Y.M. & Alam, P. (2014): Wastewater Treatment and Management in Rural areas - A Case Study of Rajouri District, Jammu and Kashmir, India, International Journal of Development Research, 4 (11), 2266-2269. [15] APHA, (1989). Standard methods for the examination of water and wastewater, American Public Health Association, Washington, D.C., 18th edn [16] WHO. (1996). Guidelines for the Safe Use of Wastewater, Excreta and Greywater, Volume 1: Policy and Regulatory Aspects. World Health Organization. [17] McLean, E.O. (1982). Soil pH and lime requirement. Methods of soil analysis, Part 2, chemical and microbiological properties, (methodsofsoilan2), 199-224 [18] Fang, H.H., & Liu, H (2002). Effect of pH on hydrogen production from glucose by a mixed culture. Bioresource technology, 82(1), 87-93. [19] Omar, A.F., & Jafri, M.Z.M (2015). Optical system in measurement of water turbidity: Design and Analytical Approach (Penerbit USM). Penerbit USM. [20] Manual, E.G (1999). Alternative Disinfectants and oxidants Guiance Manual. US EPA. [21] Mor S, Vischhe A, Ravindra K, Dahiya RP, Chandra A, Van Cleemput O (2006):Induction of enhanced methane oxidation in compost: Temperature and
  • 11. Zishan Aslam et al. Int. Journal of Engineering Research and Applications www.ijera.com ISSN: 2248-9622, Vol. 5, Issue 10, (Part - 2) October 2015, pp.69-79 www.ijera.com 79 | P a g e moisture response. Waste Manage, 26(4):381–388. [22] Wurts. A. William, (1992) “Understanding Water Hardness”, World Aquaculture, 33(1): 16-17. [23] Rowe, R. K., Quigley, R. Q. and Booker, J. R. (1995), Clay Barrier Systems for Waste Disposal Facilities, E & FN Spon, London, UK [24] Canadian Council of Resource and Environment Ministers (1987). Total dissolved solids. In: Canadian water quality guidelines. Prepared by the Task Force on Water Quality Guidelines. Environment Canada, Ottawa, March [25] Department of National Health and Welfare (1993). Water treatment principles and applications: a manual for the production of drinking water. Canadian Water and Wastewater Association [26] Clark, J.W., Viessman, W., Jr. and Hammer, M.J (1977). Water supply and pollution control. 3rd edition. Harper & Row Publishers, New York, NY [27] Water Environment Federation (2010): Design of Municipal Wastewater Treatment Plants: WEF Manual of Practice No. 8 ASCE Manuals and Reports on Engineering Practice No. 76, Fifth Edition