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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072
2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 526
Water Quality Analysis of Avaragere Lake-A Case Study
Kiran Kumar H S, Bharatharaj Etigi Y B2, Varun B K3 ,Punith C G4
1, 2, 3,4Assistant Professor, Civil Engineering Department, GMIT Davanagere, Karnataka, India
-------------------------------------------------------------------------***------------------------------------------------------------------------
Abstract – The present investigation was carried out in
Avaragere Lake, it belongs to Davanagere taluk and district,
Karnataka. The investigation deals with the physico-
chemical parameters of Avaragere Lake. Twenty two
physical and chemical parameters of water samples were
analyzed to know the bi monthly changes inturbidity, TDS,
pH, DO, Totalhardness, chlorides, alkanity, phosphates,
nitrates and certain heavy metals were analyzed for a
period of two months from Feb. 2013 to April 2013.The
results show fluctuations throughout the sampling periods.
Higher amount of alkalinity, pH, TDS, poor DO and the
parameters were within the permissible limits. The lake was
found to be under the influence of major parameters like
nitrate, pH, chlorides, TDS, calcium, magnesium and two or
more parameters have been reported above permissible
limits of drinking water, this is due to the chemical nature of
pollutants and sediments entering in to system from various
point and non-point sources .The overall investigation
results indicate that The tank is non-polluted and can be
used for domestic, irrigation and fisheries and even it is fit
for potability.
Key Words: DO, pH, TDS, Turbidity, point source, on point
source
1. INTRODUCTION
Water along with land is most important natural resources
gifted to man by nature the proper combination of these
two primary resources in space and time sets the upper
limit of the population and carrying capacity of the area.
Population also influences the quality and availability of
water resources for human use. Lack of community
perception, irrational use, widespread negligence for
conservation among various stake holders, systematic
encroachment of water bodies made them merely a dump
yard for domestic and industrial waste.
Water is very essential and precious natural resources for
sustaining life of this planet. Owing to the increase in
population and indiscriminate utilization, this vital
resource is now under tremendous pressure. In the rural
areas the water quality of lakes is being deteriorated due
to human and other biological activities. The provision of
safe drinking water reduces the incidences of many water
borne diseases. The interaction of chemicals into water
may adversely affect many species of aquatic flora and
fauna.
Though, the majority of our planet is covered by water,
only a very small proportion is associated with the
continental areas to which humans are primarily confined,
of the water associated with the continents, a large
amount (more than 99%)
1.1 STUDY AREA
Avaragere Lake is located at 5km from the centre of
the city at the out skirts near JIT, Davangere beside NH-4.
Lake is located in flat terrain at 14° 24' 15'' N and 75° 54'
00'' W and at an average elevation of 560m. It is a large
and shallow lake with a surface area of 1.12m2. The lake is
1.8Km long with a mean depth of 2.44m and maximum
depth of 4.27m.
Table No – 1.1: Details of Avaragere Lake
Location Latitude - 14° 24' 15''
Longitude - 75° 54' 00''
Mean Sea Level 560 m
Distance from
Davanagere
5 Km
Village, Taluk Avaragere, Davangere
District Davangere
Volume 2.73 X 106 m3
Surface area 1.12 m2
Maximum depth 4.27 m
Mean depth 2.44 m
Length 1.8 Km
Plate No – 1.1: Satellite view of Avaragere Lake
1.2 NEED FOR THE STUDY
The problems posed by the pollution of environment due
to anthropogenic (human) activities are fast becoming a
point that should not be overlooked in today’s world.
There are tendencies that suggest that pollution of all
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072
2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 527
forms (air, water, noise) is fast becoming a modern day
evil that has come to live with us and producing in some
dangerous effect on human health and well being.
Lakes being major source of accessible freshwater require
well planned, sustainable and scientific effort to prevent
their degradation. It is an impervious to restore and
conserve lakes and intends to explore the possibility to
work in close partnership with the private sector in
protection, conservation and sustainable management of
lakes.
1.3 LAYERS OF LAKE
The critical element for understanding lake health is
phosphorus. It’s the link between what goes on in the
watershed and what happens in the lake activities that
cause erosion and sedimentation allow phosphorous from
land to be transported to lake water.
The three layers of lake depending on the lake depth are
as follows:-
1. Epillimnion
2. Metalimnion
3. Hypolimnion
1. Epillimnion:-
The warm upper waters are sunlit, wind mixed
and oxygen rich. It is at 0-30 feet lake depth.
2. Metalimnion:-
This Layer in the water column, also known as
thermo cline, acts as a thermal barrier that prevents the
interchange of nutrients between the warm appear waters
and cold bottom waters. It is at 30-36 feet lake depth.
3.Hypolimnion:-
In the cold water at the bottom of lakes, food for
most creatures is in short supply, and reduces
temperatures and light penetration prevents plants from
growing in these layers exists below the 36 feet lake
depth.
1.4 SOURCES OF POLLUTION IN LAKE
Table No – 1.2: Point sources of pollution in lake
Source Type of problem
Power plants
Combustion of fossil fuels emits
nitrogen products into
atmosphere, which are carried
down by rainfall and other
process, causing Eutrophication in
lake body.
Sewage treatment plant (STP)
Treatment process releases acids
of nitrogen and phosphorus in
effluents, which drain in water
bodies.
Industrial plants
Industrial process releases
nitrogen and phosphorus products
in efficient which drain in water
bodies.
Table No – 1.3: Non-point sources of pollution in lakes
Source Type of problem
Agriculture Forming practices, including use of
fertilizers rich in nitrogen and
phosphorus, deposit increased
amount of these nutrients in soil
run off from these farms cause
Eutrophication in water bodies.
Sewage Direct discharge of sewage from
domestic sources, not connected to
treatment plants, will eventually
make its way into water bodies.
2. MATERIALS AND METHODOLOGY
In this chapter the attempt has been made to take stock of
water sample and the physico-chemical characterization
of water and the experimental procedures for the water
quality analysis. The study was carried out for the period
of 2 months from March 2013 to April 2013 at Avaragere
Lake. For the estimation of physico-chemical parameters,
water samples were collected in monthly basis and at an
interval of 15 days between 8.a.m to 10.a.m. The sampling
stations uniformly covered the entire area of the lake
(inlet-1, inlet-2, centre, outlet-1, outlet-2 and intermediate
station).Sampling points were decided by keeping in mind
that the considered sampling points must include shallow
and deep regions of the water body, points of inflow,
outflow of water in lake, human activities.
The water samples were collected in polythene bottles,
but for the estimation of dissolved oxygen (DO) the sample
(300ml) fixed separately in BOD bottle at spot by using
Winkler’s agents, and for other remaining experiments the
water samples were immediately brought into laboratory
for estimation of various physico-chemical parameters,
like water temperature and pH were recorded at the time
of sample collection by using thermometer and packet
digital pH meter. While the other parameters such as DO,
TDS, Hardness, EC, Alkalinity, Chlorides, Phosphates,
Nitrites and various heavy metals were estimated in the
laboratory by using Indian standard procedures (Titration
method, Atomic Absorption Spectrophotometer (AAS)
and Flame photometer).
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072
2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 528
Plate No – 2.1: Water sampling locations
3. RESULTS AND DISCUSSION
The temperature of water was found to be in the range
between 28°C to 32°C. The temperature of water is one
important parameter which directly influences some
chemical reaction in aquatic ecosystem. The significant
correlation between ambient temperature and water
temperature was studied by (Ganapathi 1943, 1962 and
Verma 1967). pH of water is important for the biotic
compound because most of plant and animal species can
survive in a narrow range of pH slightly acidic to slightly
alkaline condition. The high values pH during rainy season
may be due to dilution of alkaline substances are
dissolution of atmospheric carbon dioxide (Sheikh Nisar
and Yeragi 2003).
The DO and BOD in water is temperature dependent. As it
is required to all the plants and animals for respiration,
the high temperature and low DO during summer create
favorable condition for the development of green algae
(Prakash C 1982). Chlorides in urban areas are indicators
of large amount of non-point source pollution by
pesticides, grease, oil, metals and other toxic materials.
Basically calcium, magnesium, barium etc., are responsible
for the total hardness of water. The calcium is one of the
alkaline earth metals, not known to produce any
hazardous effect on human health. The magnesium has ten
times the solubility of calcium and being bivalent, too
produces hardness. The calcium and magnesium hardness
are the two elements, which form the most abundant ions
in fresh water, WHO (1984).
The alkalinity may be due to high pH. The high pH may be
due to the hydroxide, carbonates and bicarbonates .The
greater alkalinity values may be due to the large scale use
of its banks as open latrine and consequent washing of the
excreta in and nearby water body (NarasimhaRao and Jaya
raju 2001)
3.1. Following Bar-charts show the variation of
various water quality parameters along with sampling
stations and sampling time:-
6.75
7
7.25
7.5
7.75
8
8.25
8.5
8.75
9
9.25
pH
Figure No - 3.1.1: Variation of pH along with
sampling stations and sampling time
pH
25-Feb
12-Mar
27-Mar
11-Apr
0.55
0.6
0.65
0.7
0.75
0.8
0.85
0.9
INLET-1 INLET-2 D.S CENTRE OUTLET-1OUTLET-2
E.C(m-Simen)
Figure No - 3.1.2: Variation of E.C along with
sampling stations and sampling time
ELECTRICAL CONDUCTIVITY (E.C)
25-Feb
12-Mar
27-Mar
11-Apr
0
5
10
15
20
25
30
35
40
45
50
ACIDITY(mg/ltr)
Figure No - 3.1.3: Variation of Acidity along with
sampling stations and sampling time
ACIDITY
25-Feb
12-Mar
27-Mar
11-Apr
100
150
200
250
300
350
400
450
500
ALKALINITY(mg/ltr)
Figure No - 3.1.4: Variation of Alkalinity along with
sampling stations and sampling time
ALKALINITY
25-Feb
12-Mar
27-Mar
11-Apr
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072
2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 529
10
20
30
40
50
60
70
80
90
CHLORIDE(mg/ltr)
Figure No - 3.1.5: Variation of Chloride along with
sampling stations and sampling time
CHLORIDE
25-Feb
12-Mar
27-Mar
11-Apr
10
15
20
25
30
35
40
45
50
INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2
CALCIUM(mg/ltr)
Figure No - 3.1.6: Variation of Calcium along with
sampling stations and sampling time
CALCIUM
25-Feb
12-Mar
27-Mar
11-Apr
0
2
4
6
8
10
12
INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2
MAGNESIUM(mg/ltr)
Figure No - 3.1.7: Variation of Magnesium along with
sampling stations and sampling time
MAGNESIUM
25-Feb
12-Mar
27-Mar
11-Apr
50
60
70
80
90
100
110
120
130
140
INLET-1 INLET-2 D.S CENTRE OUTLET-1OUTLET-2
TOTALHARDNESS(mg/ltr)
Figure No - 3.1.8: Variation of Total Hardness along
with sampling stations and sampling time
TOTAL HARDNESS
25-Feb
12-Mar
27-Mar
11-Apr
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
5.5
6
DISSOLVEDOXYGEN(mg/ltr)
Figure No - 3.1.9: Variation of Dissolved Oxygen
along with sampling stations and sampling time
DISSOLVED OXYGEN
25-Feb
12-Mar
27-Mar
11-Apr
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2
IRON(mg/ltr)
Figure No - 3.1.10: Variation of Iron along with
sampling stations and sampling time
IRON
25-Feb
12-Mar
27-Mar
11-Apr
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
INLET-1 INLET-2 D.S CENTRE OUTLET-1OUTLET-2
MANGANESE(mg/ltr)
Figure No - 3.1.11: Variation of Manganese along
with sampling stations and sampling time
MANGANESE
25-Feb
12-Mar
27-Mar
11-Apr
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072
2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 530
Table No3.1: Maximum and Minimum values of different
parameters
Sl.
No.
Parameters Units Results of the samples
Maximum Minimu
m
1 pH - 9.15 7.00
2 ELECTRICAL
CONDUCTIVITY
mS 0.86 0.60
3 ACIDITY mg/l 48 10
4 ALKALINITY mg/l 498 110
5 CHLORIDE mg/l 82.97 10.99
6 CALCIUM mg/l 46.40 14.40
7 MAGNESIUM mg/l 5.56 0.96
8 TOTAL HARDNESS mg/l 136 52
9 DISSOLVED
OXYGEN
mg/l 5.61 0.49
10 IRON mg/l 4.33 0.10
11 COPPER mg/l 0.03 BDL
12 MANGANESE mg/l 4.58 0.20
13 ZINC mg/l 1.42 0.03
14 SODIUM mg/l 3.72 0.92
15 BI-CARBONATE mg/l 3.30 1.14
16 SODIUM
ABSORPTION
RATIO
mg/l 3.31 1.22
* pH was found to be in the range of 7 to 9.15 which is
slightly alkaline.
* EC was found to be in the range of 0.6 to 0.86mS(milli-
Simens) which might be due to the high suspended solids.
* Acidity was found to be in the range of 10 to 48mg/ltr
and alkalinity was found to in the range of 110 to
498mg/ltr which shows that water is slightly alkaline
* Chloride was found to be in the range of 11 to 83mg/ltr
which is well within limits of BIS standards.
* Calcium was found to be in the range of 14.4 to
46.4mg/ltr which is well within limits of BIS standard.
* Magnesium was found to be in the range of 0.96 to
5.56mg/ltr which is well within limits of BIS standards.
* Total hardness was found to be in the range of 52 to
136mg/ltr which is well within limits of BIS standards.
* DO was found to be in the range of 0.49 to 5.6mg/ltr
which shows low DO concentration present in lake which
indicates that organic pollutants are more.
* Iron was found to be in the range of 0.1 to 4.33mg/ltr
which is greater than BIS standards for drinking water
quality which might be due to the surrounding geology of
the lake area.
* In addition to above parameter heavy metal analysis was
also carried out. The heavy metals like copper, manganese,
chromium, zinc, lead, cadmium, boron and sodium was
analyzed. And the result of heavy metals analysis shows
that all heavy metals are well within the limits of BIS
standards.
0
0.5
1
1.5
2
2.5
3
3.5
4
INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2
SODIUM(mg/ltr)
Figure No - 3.1.12: Variation of Sodium along with
sampling stations and sampling time
SODIUM
25-Feb
12-Mar
27-Mar
11-Apr
0
0.5
1
1.5
2
2.5
3
3.5
INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2
BI-CARBONATE(mg/ltr)
Figure No - 3.1.13: Variation of Bi-Carbonate along
with sampling stations and sampling time
BI-CARBONATE
25-Feb
12-Mar
27-Mar
11-Apr
0
0.5
1
1.5
2
2.5
3
3.5
INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2
SAR(mg/ltr)
Figure No - 3.1.14: Variation of SAR along with
sampling stations and sampling time
SODIUM ABSORPTION RATIO(SAR)
25-Feb
12-Mar
27-Mar
11-Apr
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072
2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 531
By studying all parameters it can be concluded that the
lake water is deficit in DO for all the sampling stations and
water is slightly alkaline which may be due to the
discharge of water from the surrounding irrigational
lands.
Before using this lake water for domestic purpose it has to
treated by suitable treatment method.
4. CONCLUSIONS
1. The initial condition of the lake was studied which
shows that the water is turbid even in shallow depths due
to the presence of excess of suspended, dissolved and
colloidal solids present in the lake water.
2. The depth of the lake in past was more compared to
present .As the depth of the lake is decreased the carrying
capacity of the lake is reduced which is due to the entry of
sediments entering the lake.
3. The physico chemical analysis of results revealed that
the acidity and alkalinity of the lake is within permissible
limits in comparison with the BIS Drinking water
standards.
4. Hardness of the water is found to be within BIS
standards.
5. Studies revealed that as of now the lake water is not
used for potable use but the water can be effectively used
for potable uses with the proper treatment methods which
will treat the water to acceptable drinking water
standards as the city is facing shortage of water.
6. It can be concluded finally that after the analysis of
physico chemical attributes the water can be used for both
drinking and Irrigation purposes but with adequate
treatment to bring down the water quality to acceptable
standards.
From the above conclusions It can be suggested that the
water quality of lake is getting detoriated. It is very much
necessary to rejuvenate the lake and protect the lake from
getting polluted due to the pollutants entering into Lake
4.1 SCOPE FOR FUTURE STUDY
(1) Seasonal analysis of lake water can be done to know
the seasonal variations of the water quality parameters.
(2) Sediment analysis of the lake can be done to know the
level and kind of pollutants entering the lake.
(3) In the present study sampling on the water is carried
out in topmost layers.
REFERENCES
(1) A.G. Deviprasad, Siddaraju Kothathi. “Application of
CCME Water quality index to lake of mandya, Karnataka,
India”., International Inter disciplinary research journal
Jan-Feb-2012
(2) Aboud S Jumbe, N. Nandini, Sucharita Tandon, Sunita
N. ”Bangalore Lakes Issues and perspectives onpollution,
restoration and Management”., 1699-1706
(3) Basavaraja Simpi, S.M. Hiremath, K.N.S Murthy, K.N.
Chandrashekarappa, Anil N Patel, E.T Puttiah. “Analysis of
water quality using physico-chemical parameters
Hosahalli Tank in Shimoga District, Karnataka, India”.,
Global Journals INC(USA) , 2001
(4) Bridgton. ”Lakes Environmental Association, Water
Testing Report”
(5)Egwuonwa C.C, Uzoije A.P, Okafor V.C, Ezeanya M.C and
Nwachukwu M.U.”Evolution of the effects of industrial
waste water discharge on surface water (A Case study of
Niegeria Breweries P/C Enugu)., Greener Journal of
Physical sciences
(6) Farhana Ali and M. Musaddique. “Comparitive Analysis
of Physico-chemical and Bacteriological properties of
Eutrophic and fresh water bodies”.,
J.Aqua.Biol.Vol.24(1):57-60, 2009
(7) Infrastructure Development Corporation (Karnataka)
Limited. “Development of Lake Conservation Project,
Karnataka”
(8)K. Khelchandra Singh, B. Manihar Sharma and K.H.
Usha. “Echology of Kharungpat Lake, Thoubal, Manipur,
India: Part-1 water quality status”., The Ecoscan 4(2 &
3):241-245, 2010.
(9) K. Sahu, A. Mehta, Sangeeta Sing and Shruthi
Shukla.“Physico-chemical and Bacterological Studies of
Daphrin Hostipal Discharge at Sagar, Madhyapradesh”.,
Asian.J.Exp.Sci.Vol.No.2, 2007
(10) Masse and Miller Consulting Ltd. “Windermere Lake
Water Quality Monitoring Program and Literature
Review”., Nov-2005
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072
2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 532
BIOGRAPHIES
Working as an assistant professor
in the department of Civil
Engineering ,GMIT, Davanagere,
Research Scholar in VTU Belgaum
and working in the area of water
and waste water pollution
prevention and treatment
Engineering. Life member of
Indian Society of Technical
Education (ISTE).
Working as an assistant professor
in the department of Civil
Engineering, GMIT, Davanagere
from past 15 years of Teaching
and Research Scholar in VTU
Belgaum and working in the area
of Eco-friendly concrete. Life
member of Indian Society of
Technical Education(ISTE).
Working as an assistant professor
in the department of Civil
Engineering, GMIT, Davanagere,
Research Scholar in VTU Belgaum
and working in the area of Eco-
friendly concrete. Life member of
Indian Society of Technical
Education(ISTE).
Working as an assistant professor
in the department of Civil
Engineering,GMIT, Davanagere.
Life member of Indian Society of
Technical Education(ISTE).
3rd

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IRJET- Water Quality Analysis of Avaragere Lake- A Case Study

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072 2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 526 Water Quality Analysis of Avaragere Lake-A Case Study Kiran Kumar H S, Bharatharaj Etigi Y B2, Varun B K3 ,Punith C G4 1, 2, 3,4Assistant Professor, Civil Engineering Department, GMIT Davanagere, Karnataka, India -------------------------------------------------------------------------***------------------------------------------------------------------------ Abstract – The present investigation was carried out in Avaragere Lake, it belongs to Davanagere taluk and district, Karnataka. The investigation deals with the physico- chemical parameters of Avaragere Lake. Twenty two physical and chemical parameters of water samples were analyzed to know the bi monthly changes inturbidity, TDS, pH, DO, Totalhardness, chlorides, alkanity, phosphates, nitrates and certain heavy metals were analyzed for a period of two months from Feb. 2013 to April 2013.The results show fluctuations throughout the sampling periods. Higher amount of alkalinity, pH, TDS, poor DO and the parameters were within the permissible limits. The lake was found to be under the influence of major parameters like nitrate, pH, chlorides, TDS, calcium, magnesium and two or more parameters have been reported above permissible limits of drinking water, this is due to the chemical nature of pollutants and sediments entering in to system from various point and non-point sources .The overall investigation results indicate that The tank is non-polluted and can be used for domestic, irrigation and fisheries and even it is fit for potability. Key Words: DO, pH, TDS, Turbidity, point source, on point source 1. INTRODUCTION Water along with land is most important natural resources gifted to man by nature the proper combination of these two primary resources in space and time sets the upper limit of the population and carrying capacity of the area. Population also influences the quality and availability of water resources for human use. Lack of community perception, irrational use, widespread negligence for conservation among various stake holders, systematic encroachment of water bodies made them merely a dump yard for domestic and industrial waste. Water is very essential and precious natural resources for sustaining life of this planet. Owing to the increase in population and indiscriminate utilization, this vital resource is now under tremendous pressure. In the rural areas the water quality of lakes is being deteriorated due to human and other biological activities. The provision of safe drinking water reduces the incidences of many water borne diseases. The interaction of chemicals into water may adversely affect many species of aquatic flora and fauna. Though, the majority of our planet is covered by water, only a very small proportion is associated with the continental areas to which humans are primarily confined, of the water associated with the continents, a large amount (more than 99%) 1.1 STUDY AREA Avaragere Lake is located at 5km from the centre of the city at the out skirts near JIT, Davangere beside NH-4. Lake is located in flat terrain at 14° 24' 15'' N and 75° 54' 00'' W and at an average elevation of 560m. It is a large and shallow lake with a surface area of 1.12m2. The lake is 1.8Km long with a mean depth of 2.44m and maximum depth of 4.27m. Table No – 1.1: Details of Avaragere Lake Location Latitude - 14° 24' 15'' Longitude - 75° 54' 00'' Mean Sea Level 560 m Distance from Davanagere 5 Km Village, Taluk Avaragere, Davangere District Davangere Volume 2.73 X 106 m3 Surface area 1.12 m2 Maximum depth 4.27 m Mean depth 2.44 m Length 1.8 Km Plate No – 1.1: Satellite view of Avaragere Lake 1.2 NEED FOR THE STUDY The problems posed by the pollution of environment due to anthropogenic (human) activities are fast becoming a point that should not be overlooked in today’s world. There are tendencies that suggest that pollution of all
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072 2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 527 forms (air, water, noise) is fast becoming a modern day evil that has come to live with us and producing in some dangerous effect on human health and well being. Lakes being major source of accessible freshwater require well planned, sustainable and scientific effort to prevent their degradation. It is an impervious to restore and conserve lakes and intends to explore the possibility to work in close partnership with the private sector in protection, conservation and sustainable management of lakes. 1.3 LAYERS OF LAKE The critical element for understanding lake health is phosphorus. It’s the link between what goes on in the watershed and what happens in the lake activities that cause erosion and sedimentation allow phosphorous from land to be transported to lake water. The three layers of lake depending on the lake depth are as follows:- 1. Epillimnion 2. Metalimnion 3. Hypolimnion 1. Epillimnion:- The warm upper waters are sunlit, wind mixed and oxygen rich. It is at 0-30 feet lake depth. 2. Metalimnion:- This Layer in the water column, also known as thermo cline, acts as a thermal barrier that prevents the interchange of nutrients between the warm appear waters and cold bottom waters. It is at 30-36 feet lake depth. 3.Hypolimnion:- In the cold water at the bottom of lakes, food for most creatures is in short supply, and reduces temperatures and light penetration prevents plants from growing in these layers exists below the 36 feet lake depth. 1.4 SOURCES OF POLLUTION IN LAKE Table No – 1.2: Point sources of pollution in lake Source Type of problem Power plants Combustion of fossil fuels emits nitrogen products into atmosphere, which are carried down by rainfall and other process, causing Eutrophication in lake body. Sewage treatment plant (STP) Treatment process releases acids of nitrogen and phosphorus in effluents, which drain in water bodies. Industrial plants Industrial process releases nitrogen and phosphorus products in efficient which drain in water bodies. Table No – 1.3: Non-point sources of pollution in lakes Source Type of problem Agriculture Forming practices, including use of fertilizers rich in nitrogen and phosphorus, deposit increased amount of these nutrients in soil run off from these farms cause Eutrophication in water bodies. Sewage Direct discharge of sewage from domestic sources, not connected to treatment plants, will eventually make its way into water bodies. 2. MATERIALS AND METHODOLOGY In this chapter the attempt has been made to take stock of water sample and the physico-chemical characterization of water and the experimental procedures for the water quality analysis. The study was carried out for the period of 2 months from March 2013 to April 2013 at Avaragere Lake. For the estimation of physico-chemical parameters, water samples were collected in monthly basis and at an interval of 15 days between 8.a.m to 10.a.m. The sampling stations uniformly covered the entire area of the lake (inlet-1, inlet-2, centre, outlet-1, outlet-2 and intermediate station).Sampling points were decided by keeping in mind that the considered sampling points must include shallow and deep regions of the water body, points of inflow, outflow of water in lake, human activities. The water samples were collected in polythene bottles, but for the estimation of dissolved oxygen (DO) the sample (300ml) fixed separately in BOD bottle at spot by using Winkler’s agents, and for other remaining experiments the water samples were immediately brought into laboratory for estimation of various physico-chemical parameters, like water temperature and pH were recorded at the time of sample collection by using thermometer and packet digital pH meter. While the other parameters such as DO, TDS, Hardness, EC, Alkalinity, Chlorides, Phosphates, Nitrites and various heavy metals were estimated in the laboratory by using Indian standard procedures (Titration method, Atomic Absorption Spectrophotometer (AAS) and Flame photometer).
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072 2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 528 Plate No – 2.1: Water sampling locations 3. RESULTS AND DISCUSSION The temperature of water was found to be in the range between 28°C to 32°C. The temperature of water is one important parameter which directly influences some chemical reaction in aquatic ecosystem. The significant correlation between ambient temperature and water temperature was studied by (Ganapathi 1943, 1962 and Verma 1967). pH of water is important for the biotic compound because most of plant and animal species can survive in a narrow range of pH slightly acidic to slightly alkaline condition. The high values pH during rainy season may be due to dilution of alkaline substances are dissolution of atmospheric carbon dioxide (Sheikh Nisar and Yeragi 2003). The DO and BOD in water is temperature dependent. As it is required to all the plants and animals for respiration, the high temperature and low DO during summer create favorable condition for the development of green algae (Prakash C 1982). Chlorides in urban areas are indicators of large amount of non-point source pollution by pesticides, grease, oil, metals and other toxic materials. Basically calcium, magnesium, barium etc., are responsible for the total hardness of water. The calcium is one of the alkaline earth metals, not known to produce any hazardous effect on human health. The magnesium has ten times the solubility of calcium and being bivalent, too produces hardness. The calcium and magnesium hardness are the two elements, which form the most abundant ions in fresh water, WHO (1984). The alkalinity may be due to high pH. The high pH may be due to the hydroxide, carbonates and bicarbonates .The greater alkalinity values may be due to the large scale use of its banks as open latrine and consequent washing of the excreta in and nearby water body (NarasimhaRao and Jaya raju 2001) 3.1. Following Bar-charts show the variation of various water quality parameters along with sampling stations and sampling time:- 6.75 7 7.25 7.5 7.75 8 8.25 8.5 8.75 9 9.25 pH Figure No - 3.1.1: Variation of pH along with sampling stations and sampling time pH 25-Feb 12-Mar 27-Mar 11-Apr 0.55 0.6 0.65 0.7 0.75 0.8 0.85 0.9 INLET-1 INLET-2 D.S CENTRE OUTLET-1OUTLET-2 E.C(m-Simen) Figure No - 3.1.2: Variation of E.C along with sampling stations and sampling time ELECTRICAL CONDUCTIVITY (E.C) 25-Feb 12-Mar 27-Mar 11-Apr 0 5 10 15 20 25 30 35 40 45 50 ACIDITY(mg/ltr) Figure No - 3.1.3: Variation of Acidity along with sampling stations and sampling time ACIDITY 25-Feb 12-Mar 27-Mar 11-Apr 100 150 200 250 300 350 400 450 500 ALKALINITY(mg/ltr) Figure No - 3.1.4: Variation of Alkalinity along with sampling stations and sampling time ALKALINITY 25-Feb 12-Mar 27-Mar 11-Apr
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072 2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 529 10 20 30 40 50 60 70 80 90 CHLORIDE(mg/ltr) Figure No - 3.1.5: Variation of Chloride along with sampling stations and sampling time CHLORIDE 25-Feb 12-Mar 27-Mar 11-Apr 10 15 20 25 30 35 40 45 50 INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2 CALCIUM(mg/ltr) Figure No - 3.1.6: Variation of Calcium along with sampling stations and sampling time CALCIUM 25-Feb 12-Mar 27-Mar 11-Apr 0 2 4 6 8 10 12 INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2 MAGNESIUM(mg/ltr) Figure No - 3.1.7: Variation of Magnesium along with sampling stations and sampling time MAGNESIUM 25-Feb 12-Mar 27-Mar 11-Apr 50 60 70 80 90 100 110 120 130 140 INLET-1 INLET-2 D.S CENTRE OUTLET-1OUTLET-2 TOTALHARDNESS(mg/ltr) Figure No - 3.1.8: Variation of Total Hardness along with sampling stations and sampling time TOTAL HARDNESS 25-Feb 12-Mar 27-Mar 11-Apr 0 0.5 1 1.5 2 2.5 3 3.5 4 4.5 5 5.5 6 DISSOLVEDOXYGEN(mg/ltr) Figure No - 3.1.9: Variation of Dissolved Oxygen along with sampling stations and sampling time DISSOLVED OXYGEN 25-Feb 12-Mar 27-Mar 11-Apr 0 0.5 1 1.5 2 2.5 3 3.5 4 4.5 INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2 IRON(mg/ltr) Figure No - 3.1.10: Variation of Iron along with sampling stations and sampling time IRON 25-Feb 12-Mar 27-Mar 11-Apr 0 0.5 1 1.5 2 2.5 3 3.5 4 4.5 5 INLET-1 INLET-2 D.S CENTRE OUTLET-1OUTLET-2 MANGANESE(mg/ltr) Figure No - 3.1.11: Variation of Manganese along with sampling stations and sampling time MANGANESE 25-Feb 12-Mar 27-Mar 11-Apr
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072 2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 530 Table No3.1: Maximum and Minimum values of different parameters Sl. No. Parameters Units Results of the samples Maximum Minimu m 1 pH - 9.15 7.00 2 ELECTRICAL CONDUCTIVITY mS 0.86 0.60 3 ACIDITY mg/l 48 10 4 ALKALINITY mg/l 498 110 5 CHLORIDE mg/l 82.97 10.99 6 CALCIUM mg/l 46.40 14.40 7 MAGNESIUM mg/l 5.56 0.96 8 TOTAL HARDNESS mg/l 136 52 9 DISSOLVED OXYGEN mg/l 5.61 0.49 10 IRON mg/l 4.33 0.10 11 COPPER mg/l 0.03 BDL 12 MANGANESE mg/l 4.58 0.20 13 ZINC mg/l 1.42 0.03 14 SODIUM mg/l 3.72 0.92 15 BI-CARBONATE mg/l 3.30 1.14 16 SODIUM ABSORPTION RATIO mg/l 3.31 1.22 * pH was found to be in the range of 7 to 9.15 which is slightly alkaline. * EC was found to be in the range of 0.6 to 0.86mS(milli- Simens) which might be due to the high suspended solids. * Acidity was found to be in the range of 10 to 48mg/ltr and alkalinity was found to in the range of 110 to 498mg/ltr which shows that water is slightly alkaline * Chloride was found to be in the range of 11 to 83mg/ltr which is well within limits of BIS standards. * Calcium was found to be in the range of 14.4 to 46.4mg/ltr which is well within limits of BIS standard. * Magnesium was found to be in the range of 0.96 to 5.56mg/ltr which is well within limits of BIS standards. * Total hardness was found to be in the range of 52 to 136mg/ltr which is well within limits of BIS standards. * DO was found to be in the range of 0.49 to 5.6mg/ltr which shows low DO concentration present in lake which indicates that organic pollutants are more. * Iron was found to be in the range of 0.1 to 4.33mg/ltr which is greater than BIS standards for drinking water quality which might be due to the surrounding geology of the lake area. * In addition to above parameter heavy metal analysis was also carried out. The heavy metals like copper, manganese, chromium, zinc, lead, cadmium, boron and sodium was analyzed. And the result of heavy metals analysis shows that all heavy metals are well within the limits of BIS standards. 0 0.5 1 1.5 2 2.5 3 3.5 4 INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2 SODIUM(mg/ltr) Figure No - 3.1.12: Variation of Sodium along with sampling stations and sampling time SODIUM 25-Feb 12-Mar 27-Mar 11-Apr 0 0.5 1 1.5 2 2.5 3 3.5 INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2 BI-CARBONATE(mg/ltr) Figure No - 3.1.13: Variation of Bi-Carbonate along with sampling stations and sampling time BI-CARBONATE 25-Feb 12-Mar 27-Mar 11-Apr 0 0.5 1 1.5 2 2.5 3 3.5 INLET-1 INLET-2 D.S CENTRE OUTLET-1 OUTLET-2 SAR(mg/ltr) Figure No - 3.1.14: Variation of SAR along with sampling stations and sampling time SODIUM ABSORPTION RATIO(SAR) 25-Feb 12-Mar 27-Mar 11-Apr
  • 6. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072 2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 531 By studying all parameters it can be concluded that the lake water is deficit in DO for all the sampling stations and water is slightly alkaline which may be due to the discharge of water from the surrounding irrigational lands. Before using this lake water for domestic purpose it has to treated by suitable treatment method. 4. CONCLUSIONS 1. The initial condition of the lake was studied which shows that the water is turbid even in shallow depths due to the presence of excess of suspended, dissolved and colloidal solids present in the lake water. 2. The depth of the lake in past was more compared to present .As the depth of the lake is decreased the carrying capacity of the lake is reduced which is due to the entry of sediments entering the lake. 3. The physico chemical analysis of results revealed that the acidity and alkalinity of the lake is within permissible limits in comparison with the BIS Drinking water standards. 4. Hardness of the water is found to be within BIS standards. 5. Studies revealed that as of now the lake water is not used for potable use but the water can be effectively used for potable uses with the proper treatment methods which will treat the water to acceptable drinking water standards as the city is facing shortage of water. 6. It can be concluded finally that after the analysis of physico chemical attributes the water can be used for both drinking and Irrigation purposes but with adequate treatment to bring down the water quality to acceptable standards. From the above conclusions It can be suggested that the water quality of lake is getting detoriated. It is very much necessary to rejuvenate the lake and protect the lake from getting polluted due to the pollutants entering into Lake 4.1 SCOPE FOR FUTURE STUDY (1) Seasonal analysis of lake water can be done to know the seasonal variations of the water quality parameters. (2) Sediment analysis of the lake can be done to know the level and kind of pollutants entering the lake. (3) In the present study sampling on the water is carried out in topmost layers. REFERENCES (1) A.G. Deviprasad, Siddaraju Kothathi. “Application of CCME Water quality index to lake of mandya, Karnataka, India”., International Inter disciplinary research journal Jan-Feb-2012 (2) Aboud S Jumbe, N. Nandini, Sucharita Tandon, Sunita N. ”Bangalore Lakes Issues and perspectives onpollution, restoration and Management”., 1699-1706 (3) Basavaraja Simpi, S.M. Hiremath, K.N.S Murthy, K.N. Chandrashekarappa, Anil N Patel, E.T Puttiah. “Analysis of water quality using physico-chemical parameters Hosahalli Tank in Shimoga District, Karnataka, India”., Global Journals INC(USA) , 2001 (4) Bridgton. ”Lakes Environmental Association, Water Testing Report” (5)Egwuonwa C.C, Uzoije A.P, Okafor V.C, Ezeanya M.C and Nwachukwu M.U.”Evolution of the effects of industrial waste water discharge on surface water (A Case study of Niegeria Breweries P/C Enugu)., Greener Journal of Physical sciences (6) Farhana Ali and M. Musaddique. “Comparitive Analysis of Physico-chemical and Bacteriological properties of Eutrophic and fresh water bodies”., J.Aqua.Biol.Vol.24(1):57-60, 2009 (7) Infrastructure Development Corporation (Karnataka) Limited. “Development of Lake Conservation Project, Karnataka” (8)K. Khelchandra Singh, B. Manihar Sharma and K.H. Usha. “Echology of Kharungpat Lake, Thoubal, Manipur, India: Part-1 water quality status”., The Ecoscan 4(2 & 3):241-245, 2010. (9) K. Sahu, A. Mehta, Sangeeta Sing and Shruthi Shukla.“Physico-chemical and Bacterological Studies of Daphrin Hostipal Discharge at Sagar, Madhyapradesh”., Asian.J.Exp.Sci.Vol.No.2, 2007 (10) Masse and Miller Consulting Ltd. “Windermere Lake Water Quality Monitoring Program and Literature Review”., Nov-2005
  • 7. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 12 | Dec 2018 www.irjet.net p-ISSN: 2395-0072 2018, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 532 BIOGRAPHIES Working as an assistant professor in the department of Civil Engineering ,GMIT, Davanagere, Research Scholar in VTU Belgaum and working in the area of water and waste water pollution prevention and treatment Engineering. Life member of Indian Society of Technical Education (ISTE). Working as an assistant professor in the department of Civil Engineering, GMIT, Davanagere from past 15 years of Teaching and Research Scholar in VTU Belgaum and working in the area of Eco-friendly concrete. Life member of Indian Society of Technical Education(ISTE). Working as an assistant professor in the department of Civil Engineering, GMIT, Davanagere, Research Scholar in VTU Belgaum and working in the area of Eco- friendly concrete. Life member of Indian Society of Technical Education(ISTE). Working as an assistant professor in the department of Civil Engineering,GMIT, Davanagere. Life member of Indian Society of Technical Education(ISTE). 3rd