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V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com
ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08
www.ijera.com 5 | P a g e
Seasonal Variation of Groundwater Quality in Parts of Y.S.R and
Anantapur Districts, Andhra Pradesh, India
V. Sunitha*, J. Abdullah Khan**, M. Prasad***, M. Ramakrishna Reddy****
*(Asst. Professor, Department of Geology, Yogi Vemana University, Kadapa -516003
**( Research Scholar, Department of Geology, Yogi Vemana University, Kadapa -516003
*** (Research Scholar, Department of Earth Sciences, Yogi Vemana University, Kadapa -516003
**** (Professor, Department of Earth Sciences, Yogi Vemana University, Kadapa -516003
ABSTRACT
Groundwater is used for domestic, industrial water supply and for irrigation all over the world. The groundwater
quality is a function of natural processes as well as anthropogenic activities. The safe potable water is
enormously essential for living and groundwater is one of the sources for human consumption in both urban as
well as rural areas. The area is located in the survey of India toposheet Number 57 J/3 lying between east
780
00’
0’’
to 780
15’
0”
longitudes and 140
15’
0’’
to 140
30’
0’’
North latitudes covering an area of 720 sq. kms.
Geologically, it is underlain mainly by Peninsular gneisses of Archean age followed by Gulcheru and Vemapalli
formations comprising quartzites, conglomerates, dolomites and shales. Major geomorphic units are
denudational hills, residual hills, pediments, pediplains, structural hills and valleys. The study area experiences a
semiarid climate. Physicochemical parameters viz., pH, total hardness, calcium, chloride, total dissolved solids,
fluoride were analyzed. Most of parameter show higher value than permissible limit in pre and post monsoon.
Further, a moderation in water quality was observed after the monsoon season, which can be attributed to a
possible dilution due to groundwater recharge People dependent on this water may prone to health hazard.
Therefore some effective measures are urgently required to enhance the quality of water in these areas.
Keywords – Seasonal variation, Groundwater quality, Y.S.R, Anantapur Districts
I. INTRODUCTION
Water is indispensable and one the precious
natural resource of our planet. Ground water is an
important natural source of water supply all over the
world. Water is the elixir of life and living
organisms can’t survive for short duration without
water. It is a widespread solvent and as a solvent it
provides the ionic balance and nutrients, which
maintain all forms of life [1]. Particularly
Groundwater plays a pivotal role in human life and
development. There are several states in India where
more than 90% populations are dependent on
groundwater for drinking and other purposes [2, 3].
Groundwater is generally considered to be much
cleaner than surface water. Nevertheless, several
factors such as discharge of industrial, agricultural
and household water, land use practices, geological
formation, rainfall patterns, and infiltration rate
affect the groundwater quality [4]. Thus
groundwater possess little amount of soluble salts.
The kind and quality of these salts depend upon the
sources for recharge of the groundwater and the
strata through which it flows. An excess of soluble
salts can be injurious for many crops. Hence, an
understanding of the chemistry of groundwater is
essential to properly evaluate groundwater quality
for drinking and agricultural purposes [5]. Its use in
irrigation , industries and domestic usage continues
to increase where perennial surface water source are
absent [6] The modern civilization, over
exploitation, rapid industrialization and increased
population have lead to fast degradation of our
environment [7]. To meet the rising demand it is
imperative to recognize the fresh water resources
and also to find out remedial methods for
improvement of water quality [8].The quality of
water may depend on geology of particular area and
also vary with depth of water table and seasonal
changes and is governed by the extent and
composition of the dissolved salts depending upon
source of the salt and soil, subsurface environment.
Ground water resources are dynamic in nature and
are affected by factors of irrigation activities,
industrialization, urbanization and geological
processes occurring within them and reactions with
aquifer minerals [9,10], rainfall patterns, infiltration
rate, leaching of pollutants from the landfill[11].
II. STUDY AREA
The study area lies between Pulivendula
and Sanivaripalli situated between parallels of
780
00’
0’’
to 780
15’
0”
E longitude and 140
15’
0’’
to
140
30’
0’’
N latitude with intended boundary falling in
Survey of India (SOI) topographic sheet # 57J/03 on
1:50,000 scale covering an area of 720 sq. kms. The
RESEARCH ARTICLE OPEN ACCESS
V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com
ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08
www.ijera.com 6 | P a g e
study area includes five revenue mandals namely,
Pulivendula, Lingala, Uduma kurti, Krishnam
garipalli, and Sanivaripalli and is shown in figure-1.
The central and southern part of study area is
occupied by high hills, ridges and valleys. The
value of contours in the study area ranges from 200-
600 m. The slope category is within 1-15 degrees.
The Maddaleru is the only seasonal river fed by
monsoon which is flowing in the NW direction in
the southernal part of the study area. The climate is
dry with mean annual rainfall of 100-150 cm and
mean annual temperature of 320
C. The month of
May is considered to be the hottest (450
C) while
December is considered to be the coldest (250
C).
III. METHODOLOGY
In the present study, water samples were
collected from twenty tube wells in the study area.
The study is carried out with the help of topographic
sheets, Garmin e Trex H (GPS) receiver, Arc GIS
9.3 and fieldwork. Toposheets are used to prepare
the basemap, drainage map and to understand the
general nature of the study area. GPS is used to map
the location of each sampling well and finally the
results were taken to the GIS for further analysis.
The field work included water level measurements,
well inventory and collection of water samples from
tube wells and the study of geological and
geomorphological features of the area in general.
The groundwater samples collected during June
2011 were analyzed, as per the procedure of APHA
(1995), and suggested precautions were taken to
avoid contamination. The various parameters
determined were: pH, total hardness (TH), chloride
(Cl-
), calcium (Ca+2
) and fluoride (F-
). pH was
determined by pH meter; TH, Cl-
, Ca+2
by titrimetry;
F-
was determined by using ion selective electrode
(Orion 4 star ion meter, Model: pH/ISE). The
location of each wells were taken into the GIS
environment and the results of each parameters
analysed were added to the concerned wells.
IV. RESULTS AND DISCUSSION:
The results of chemical and statistical
parameters analyzed are given in Table 1 & 2(pre
and post monsoon respectively). Understanding the
quality of groundwater is as important because it is
the main factor determining its suitability for
drinking, domestic, agricultural and industrial
purposes.
The measurement of pH is one of the most
frequently used tests in water chemistry. The
groundwater quality in the study area of alkaline
type. The pH value is ranges from 6.1 to8.2 in pre
monsoon, 6.0 to 8 in post monsoon season. Most of
the samples are alkaline in nature except only one
station (Ambakpalli) in both pre and post monsoons
as acidic in nature. pH values of remaining samples
are within the permissible limit
The Electrical Conductivity range in post
monsoon, pre monsoon and monsoon is 490 to 720
μS/cm, and 450.0 to 640 μS/cm respectively. There
is no prescribed standard suggested by WHO. The
EC value is completely depends on the TDS value if
TDS is increases the EC value will increase. But the
high EC value indicates the more salts in the
groundwater.
The total dissolved solids are the sum of
total cations and anions. It includes the total ionic
species such as sodium, potassium, calcium,
magnesium, chloride, bicarbonate, nitrate, sulphate
and other trace elements [12]. The TDS range in post
monsoon, pre monsoon and monsoon is 314 to 461
mg/L, and 288 to 410 mg/L respectively. Most of the
samples are above the permissible limit. It may be
due to the agricultural runoff. Water with high
dissolved solids generally has inferior palatability
and may induce an unfavourable physiological
reaction in the person who drinks it. Highly
mineralized water is also unsuitable for many
industrial applications [13, 14].
Total hardness is caused primarily by the
presence of cations such as calcium and magnesium
and anions such as carbonates and bicarbonates,
chloride and sulphate in water Water hardness has
no known adverse effects; however, some evidence
indicates its role in heart disease [15]. Total
Hardness was varied between 60 to 180 mg/L in pre
and 50 to 170 mg/L in post monsoon. Most of the
samples are above the permissible limit.
Calcium range in post monsoon, pre
monsoon is 8 to 992 mg/L and 8 to 900 mg/L
respectively. Few samples are above the permissible
limit in two seasons. The high concentration of
calcium may be due the dissolution of limestone,
dolomite.
The chloride range in post monsoon and pre
monsoon is 18 to 167 mg/L, 16 to 160 mg/L
respectively. Most of the samples are above the
permissible limit in three seasons. The high value is
may be due to the discharge of domestic sewage and
agricultural waste into ground. And Soil porosity
and permeability also has a key role in building up
the chloride concentration [18].
The Fluoride range in post monsoon, pre
monsoon and monsoon is 0.1 to 6.7 mg/L and 0.1 to
6.6 mg/L respectively. Most of the samples are
above the permissible limit in two seasons.
V. CONCLUSION
The water quality parameter like pH, EC,
total dissolved solid, total hardness, calcium,
chloride and Fluoride are found to be high value in
most of the sample at both seasons. The pH value is
ranges from 6.1 to 8.2 in pre monsoon, 6.0 to 8 in
V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com
ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08
www.ijera.com 7 | P a g e
post monsoon season. The Electrical Conductivity
range in post monsoon, pre monsoon and monsoon
is 490 to 720 μS/cm, and 450.0 to 640 μS/cm
respectively. The TDS range in pre monsoon and
post monsoon is 314 to 461 mg/L, and 288 to 410
mg/L respectively. Total Hardness was varied
between 60 to 180 mg/L in pre and 50 to 170 mg/L
in post monsoon. Most of the samples are above the
permissible limit. Calcium range in post monsoon,
pre monsoon and monsoon is 8 to 992 mg/L and 8 to
900 mg/L. The chloride range in post monsoon, pre
monsoon and monsoon is 18 to 167 mg/L and 16 to
160 mg/L respectively. The Fluoride range in post
monsoon, pre monsoon and monsoon is 0.1 to 6.7
mg/L and 0.1 to 6.6 mg/L. All the water quality
parameters analyzed in this study showed a
perceptible moderation in the post monsoon
observations. This dilution may be attributed to
replenishment of the groundwater by rainfall during
the monsoon season.
ACKNOWLEDGEMENTS
This research has been financed by
Department of Science and Technology (DST-
INSPIRE), government of India; INSPIRE
fellowship under AORC, sanctioned to second
author which is gratefully acknowledged.
REFERENCES
[1]. Biswajit Raj, Jr. Environ. Poll, 2001, 8(4),
329-332
[2]. Dinesh Kumar Tank and Singh Chandel CP
, Nature & Science, 2010, 8(10).1-7
[3]. Ramachandraiah C , Centre for Economic
and Social Studies, 2004, 56
[4]. Patil VT, Patil PR, J Environ Sci Tech,
2010, 5, 274–290
[5]. Saumitra Mukherjee, Bir Abhimanyu
Kumar, László Körtvélyessy, Journal of
Environmental Hydrology,13 Paper 2005
15, 2.
[6]. C.R. Mariappan, G. Govindaraj, S. Vinoth
Rathen, G. Vijaya Prakash, Preparation,
characterization, ac conductivity and
permittivity studies on vitreous
M4AlCdP3O12 (M = Li, Na, K) system
Mater. Sci. Eng. B 2005, 121 2.
[7]. K Murli R D , Swasthik and R. Elangovan ;
Assessment of ground water quality in
coimbatore south Taluk ,coimbatore
District,India. A WQI approach., 10 (4) 52
[8]. Ch. Maruthi Devi and T .Usha Madhuri A
study on Ground water Quality in Pakistan
district and its suitability for drinking nept.
2011,10 (3), 481- 483;.
[9]. Chartterjee, R.; Tarafder, G.; Paul S.,
Groundwater quality assessment of
Dhanbad District, District, Jharkhand,
India, Bull. Eng. Geol. Environ. 2010,
69:137-141
[10]. Nagarajan, R.; Rajmohan, N.; Mahendran,
U.; Senthamilkumar, S., Evaluation of
groundater quality and its suitability for
drinking and agricultural use in Thanjavur
city, Tamil Nadu, India, Environ. Monit.
Assess. 2010, 171(1-4289-308
[11]. Srivastava, S. K; Ramanathan, A. L.,
Geochemical assessment of groundwater
quality in vicinity of Bhalswa landfill,
Delhi, India, using graphical and
multivariate statistical methods.
Environmental Geology, 2008, 53, 1509–
1528
[12]. Mondal, N.C., Saxena, V.K. and Singh,
V.S, , Environmental Geology, 2005, 48,
149-157
[13]. Trivedy R.K. and Goel P.K, Chemical on
biological methods for water pollution
studies, Environmental Publications, Karad,
1986
[14]. Raja G. and Venkatesan P, E.Journal of
Chemistry, 2010, 7(2), 473-478
[15]. Schroeder HA. Relations between hardness
of water and death rates from certain
chronic and degenerative diseases in the
United States. J Chron disease. 12, 1960,
586-591.
[16]. Rao, S.N, National Seminar on Hydrology
of Precambrian Terrains and Hard Rock
Areas, 1997 129-134
[17]. Chadha, D.K, Hydrogeology Journal, 1999,
7(5), 431-439.
Figure 1: Study area location map
V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com
ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08
www.ijera.com 8 | P a g e
S. No Village Name pH EC TDS TH mg/L Ca+2
mg/L Cl-
mg/L F-
mg/L
1 Kottala 7.9 680 435 100 104 32 0.2
2 Gajjalapalli - 1 7.8 590 378 140 88 128 1.5
3 Gajjalapalli - 2 7.4 580 371 160 16 110 6.7
4 Gajjalapalli - 3 7.6 490 314 100 8 92 4
5 Malakavemula 8.2 620 397 80 32 57 1.9
6 Sanevaripalli 8 630 403 140 48 131 1.7
7 Kotareddypalli 7.9 520 333 100 16 67 3.8
8 Vaddekindi tanda 8.2 630 403 100 240 64 2.7
9 Mallepalli 7.1 640 409 180 64 121 2.9
10 Yogi Vemana Reservoir 8 540 346 120 992 74 2.4
11 Dorigallu 7.2 580 371 100 32 88 2.1
12 Eguvapalli 6.9 530 339 140 256 43 0.1
13 Diguvapalli 7.2 610 390 60 32 18 0.4
14 Ambakapalli 6.1 720 461 120 64 28 0.6
15 Nalagondavaripalli- 1 7.9 600 384 80 104 64 0.7
16 Nalagondavaripalli- 2 7.8 580 371 120 88 78 0.2
17 Mallikarjunapuram 8 590 378 100 80 28 0.7
18 Ippatla 7.8 650 416 180 32 160 0.5
19 Chinnakuddala 7.6 670 429 180 40 167 0.5
20 Lingala 8 530 339 180 56 100 0.3
MAX 8.2 720 461 180 992 167 6.7
MIN 6.1 490 314 60 8 18 0.1
MEAN 7.63 599 383 124 119.6 82.5 1.695
STDEV 0.51717 58.6604 37.542 37.0490 215.765 43.5968 1.69627
Table 1: Result of chemical analysis and statistical parameters of groundwater samples collected from the study
area during pre monsoon season.
S. No Village Name pH EC TDS TH mg/L Ca+2
mg/L Cl-
mg/L F-
mg/L
1 Kottala 7.6 600 384 80 100 30 0.2
2 Gajjalapalli - 1 7.4 550 352 120 80 120 1.3
3 Gajjalapalli - 2 7.2 500 320 140 16 100 6.6
4 Gajjalapalli - 3 7.2 450 288 80 8 90 3.8
5 Malakavemula 8 560 358 70 30 50 1.6
6 Sanevaripalli 7.8 580 371 130 46 130 1.5
7 Kotareddypalli 7.7 480 307 80 14 60 3.6
8 Vaddekindi tanda 8 560 358 90 220 60 2.5
9 Mallepalli 7 570 365 170 60 120 2.7
10 Yogi Vemana Reservoir 7.8 460 294 100 900 70 2.2
11 Dorigallu 7 500 320 80 30 80 2
12 Eguvapalli 6.6 460 294 130 250 40 0.1
13 Diguvapalli 7 520 333 50 30 16 0.2
14 Ambakapalli 6 640 410 100 60 26 0.3
15 Nalagondavaripalli- 1 7.7 530 339 70 100 60 0.5
16 Nalagondavaripalli- 2 7.4 520 333 100 80 70 0.2
17 Mallikarjunapuram 7.8 460 294 80 70 26 0.5
18 Ippatla 7.6 580 371 160 30 158 0.3
19 Chinnakuddala 7.4 600 384 170 40 160 0.3
20 Lingala 7.8 470 300 160 50 98 0.2
MAX 8 640 410 170 900 160 6.6
MIN 6 450 288 50 8 16 0.1
MEAN 7.4 529.5 338.88 108 110.7 78.2 1.53
STDV 0.50 56.14 35.93 36.93 196.15 43.08 1.68
Table 2: Result of chemical analysis and statistical parameters of groundwater samples collected from the study
area during post monsoon season.
S.No Parameters ISI 1983 Mean value of
parameters under analysis
Pre monsoon Post Monsoon
1 PH 6.5-8.5 7.63 7.4
2 EC - 599 529.5
3 TDS 500 383.36 338.88
4 TH 300 124 108
5 Ca+2
75 119.6 110.7
6 Cl-
250 82.5 78.2
7 F-
1.5 1.695 1.53
Table 3: Indian Standards (ISI 1983) for drinking and public health purposes.

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Seasonal Variation of Groundwater Quality in Parts of Y.S.R and Anantapur Districts, Andhra Pradesh, India

  • 1. V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08 www.ijera.com 5 | P a g e Seasonal Variation of Groundwater Quality in Parts of Y.S.R and Anantapur Districts, Andhra Pradesh, India V. Sunitha*, J. Abdullah Khan**, M. Prasad***, M. Ramakrishna Reddy**** *(Asst. Professor, Department of Geology, Yogi Vemana University, Kadapa -516003 **( Research Scholar, Department of Geology, Yogi Vemana University, Kadapa -516003 *** (Research Scholar, Department of Earth Sciences, Yogi Vemana University, Kadapa -516003 **** (Professor, Department of Earth Sciences, Yogi Vemana University, Kadapa -516003 ABSTRACT Groundwater is used for domestic, industrial water supply and for irrigation all over the world. The groundwater quality is a function of natural processes as well as anthropogenic activities. The safe potable water is enormously essential for living and groundwater is one of the sources for human consumption in both urban as well as rural areas. The area is located in the survey of India toposheet Number 57 J/3 lying between east 780 00’ 0’’ to 780 15’ 0” longitudes and 140 15’ 0’’ to 140 30’ 0’’ North latitudes covering an area of 720 sq. kms. Geologically, it is underlain mainly by Peninsular gneisses of Archean age followed by Gulcheru and Vemapalli formations comprising quartzites, conglomerates, dolomites and shales. Major geomorphic units are denudational hills, residual hills, pediments, pediplains, structural hills and valleys. The study area experiences a semiarid climate. Physicochemical parameters viz., pH, total hardness, calcium, chloride, total dissolved solids, fluoride were analyzed. Most of parameter show higher value than permissible limit in pre and post monsoon. Further, a moderation in water quality was observed after the monsoon season, which can be attributed to a possible dilution due to groundwater recharge People dependent on this water may prone to health hazard. Therefore some effective measures are urgently required to enhance the quality of water in these areas. Keywords – Seasonal variation, Groundwater quality, Y.S.R, Anantapur Districts I. INTRODUCTION Water is indispensable and one the precious natural resource of our planet. Ground water is an important natural source of water supply all over the world. Water is the elixir of life and living organisms can’t survive for short duration without water. It is a widespread solvent and as a solvent it provides the ionic balance and nutrients, which maintain all forms of life [1]. Particularly Groundwater plays a pivotal role in human life and development. There are several states in India where more than 90% populations are dependent on groundwater for drinking and other purposes [2, 3]. Groundwater is generally considered to be much cleaner than surface water. Nevertheless, several factors such as discharge of industrial, agricultural and household water, land use practices, geological formation, rainfall patterns, and infiltration rate affect the groundwater quality [4]. Thus groundwater possess little amount of soluble salts. The kind and quality of these salts depend upon the sources for recharge of the groundwater and the strata through which it flows. An excess of soluble salts can be injurious for many crops. Hence, an understanding of the chemistry of groundwater is essential to properly evaluate groundwater quality for drinking and agricultural purposes [5]. Its use in irrigation , industries and domestic usage continues to increase where perennial surface water source are absent [6] The modern civilization, over exploitation, rapid industrialization and increased population have lead to fast degradation of our environment [7]. To meet the rising demand it is imperative to recognize the fresh water resources and also to find out remedial methods for improvement of water quality [8].The quality of water may depend on geology of particular area and also vary with depth of water table and seasonal changes and is governed by the extent and composition of the dissolved salts depending upon source of the salt and soil, subsurface environment. Ground water resources are dynamic in nature and are affected by factors of irrigation activities, industrialization, urbanization and geological processes occurring within them and reactions with aquifer minerals [9,10], rainfall patterns, infiltration rate, leaching of pollutants from the landfill[11]. II. STUDY AREA The study area lies between Pulivendula and Sanivaripalli situated between parallels of 780 00’ 0’’ to 780 15’ 0” E longitude and 140 15’ 0’’ to 140 30’ 0’’ N latitude with intended boundary falling in Survey of India (SOI) topographic sheet # 57J/03 on 1:50,000 scale covering an area of 720 sq. kms. The RESEARCH ARTICLE OPEN ACCESS
  • 2. V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08 www.ijera.com 6 | P a g e study area includes five revenue mandals namely, Pulivendula, Lingala, Uduma kurti, Krishnam garipalli, and Sanivaripalli and is shown in figure-1. The central and southern part of study area is occupied by high hills, ridges and valleys. The value of contours in the study area ranges from 200- 600 m. The slope category is within 1-15 degrees. The Maddaleru is the only seasonal river fed by monsoon which is flowing in the NW direction in the southernal part of the study area. The climate is dry with mean annual rainfall of 100-150 cm and mean annual temperature of 320 C. The month of May is considered to be the hottest (450 C) while December is considered to be the coldest (250 C). III. METHODOLOGY In the present study, water samples were collected from twenty tube wells in the study area. The study is carried out with the help of topographic sheets, Garmin e Trex H (GPS) receiver, Arc GIS 9.3 and fieldwork. Toposheets are used to prepare the basemap, drainage map and to understand the general nature of the study area. GPS is used to map the location of each sampling well and finally the results were taken to the GIS for further analysis. The field work included water level measurements, well inventory and collection of water samples from tube wells and the study of geological and geomorphological features of the area in general. The groundwater samples collected during June 2011 were analyzed, as per the procedure of APHA (1995), and suggested precautions were taken to avoid contamination. The various parameters determined were: pH, total hardness (TH), chloride (Cl- ), calcium (Ca+2 ) and fluoride (F- ). pH was determined by pH meter; TH, Cl- , Ca+2 by titrimetry; F- was determined by using ion selective electrode (Orion 4 star ion meter, Model: pH/ISE). The location of each wells were taken into the GIS environment and the results of each parameters analysed were added to the concerned wells. IV. RESULTS AND DISCUSSION: The results of chemical and statistical parameters analyzed are given in Table 1 & 2(pre and post monsoon respectively). Understanding the quality of groundwater is as important because it is the main factor determining its suitability for drinking, domestic, agricultural and industrial purposes. The measurement of pH is one of the most frequently used tests in water chemistry. The groundwater quality in the study area of alkaline type. The pH value is ranges from 6.1 to8.2 in pre monsoon, 6.0 to 8 in post monsoon season. Most of the samples are alkaline in nature except only one station (Ambakpalli) in both pre and post monsoons as acidic in nature. pH values of remaining samples are within the permissible limit The Electrical Conductivity range in post monsoon, pre monsoon and monsoon is 490 to 720 μS/cm, and 450.0 to 640 μS/cm respectively. There is no prescribed standard suggested by WHO. The EC value is completely depends on the TDS value if TDS is increases the EC value will increase. But the high EC value indicates the more salts in the groundwater. The total dissolved solids are the sum of total cations and anions. It includes the total ionic species such as sodium, potassium, calcium, magnesium, chloride, bicarbonate, nitrate, sulphate and other trace elements [12]. The TDS range in post monsoon, pre monsoon and monsoon is 314 to 461 mg/L, and 288 to 410 mg/L respectively. Most of the samples are above the permissible limit. It may be due to the agricultural runoff. Water with high dissolved solids generally has inferior palatability and may induce an unfavourable physiological reaction in the person who drinks it. Highly mineralized water is also unsuitable for many industrial applications [13, 14]. Total hardness is caused primarily by the presence of cations such as calcium and magnesium and anions such as carbonates and bicarbonates, chloride and sulphate in water Water hardness has no known adverse effects; however, some evidence indicates its role in heart disease [15]. Total Hardness was varied between 60 to 180 mg/L in pre and 50 to 170 mg/L in post monsoon. Most of the samples are above the permissible limit. Calcium range in post monsoon, pre monsoon is 8 to 992 mg/L and 8 to 900 mg/L respectively. Few samples are above the permissible limit in two seasons. The high concentration of calcium may be due the dissolution of limestone, dolomite. The chloride range in post monsoon and pre monsoon is 18 to 167 mg/L, 16 to 160 mg/L respectively. Most of the samples are above the permissible limit in three seasons. The high value is may be due to the discharge of domestic sewage and agricultural waste into ground. And Soil porosity and permeability also has a key role in building up the chloride concentration [18]. The Fluoride range in post monsoon, pre monsoon and monsoon is 0.1 to 6.7 mg/L and 0.1 to 6.6 mg/L respectively. Most of the samples are above the permissible limit in two seasons. V. CONCLUSION The water quality parameter like pH, EC, total dissolved solid, total hardness, calcium, chloride and Fluoride are found to be high value in most of the sample at both seasons. The pH value is ranges from 6.1 to 8.2 in pre monsoon, 6.0 to 8 in
  • 3. V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08 www.ijera.com 7 | P a g e post monsoon season. The Electrical Conductivity range in post monsoon, pre monsoon and monsoon is 490 to 720 μS/cm, and 450.0 to 640 μS/cm respectively. The TDS range in pre monsoon and post monsoon is 314 to 461 mg/L, and 288 to 410 mg/L respectively. Total Hardness was varied between 60 to 180 mg/L in pre and 50 to 170 mg/L in post monsoon. Most of the samples are above the permissible limit. Calcium range in post monsoon, pre monsoon and monsoon is 8 to 992 mg/L and 8 to 900 mg/L. The chloride range in post monsoon, pre monsoon and monsoon is 18 to 167 mg/L and 16 to 160 mg/L respectively. The Fluoride range in post monsoon, pre monsoon and monsoon is 0.1 to 6.7 mg/L and 0.1 to 6.6 mg/L. All the water quality parameters analyzed in this study showed a perceptible moderation in the post monsoon observations. This dilution may be attributed to replenishment of the groundwater by rainfall during the monsoon season. ACKNOWLEDGEMENTS This research has been financed by Department of Science and Technology (DST- INSPIRE), government of India; INSPIRE fellowship under AORC, sanctioned to second author which is gratefully acknowledged. REFERENCES [1]. Biswajit Raj, Jr. Environ. Poll, 2001, 8(4), 329-332 [2]. Dinesh Kumar Tank and Singh Chandel CP , Nature & Science, 2010, 8(10).1-7 [3]. Ramachandraiah C , Centre for Economic and Social Studies, 2004, 56 [4]. Patil VT, Patil PR, J Environ Sci Tech, 2010, 5, 274–290 [5]. Saumitra Mukherjee, Bir Abhimanyu Kumar, László Körtvélyessy, Journal of Environmental Hydrology,13 Paper 2005 15, 2. [6]. C.R. Mariappan, G. Govindaraj, S. Vinoth Rathen, G. Vijaya Prakash, Preparation, characterization, ac conductivity and permittivity studies on vitreous M4AlCdP3O12 (M = Li, Na, K) system Mater. Sci. Eng. B 2005, 121 2. [7]. K Murli R D , Swasthik and R. Elangovan ; Assessment of ground water quality in coimbatore south Taluk ,coimbatore District,India. A WQI approach., 10 (4) 52 [8]. Ch. Maruthi Devi and T .Usha Madhuri A study on Ground water Quality in Pakistan district and its suitability for drinking nept. 2011,10 (3), 481- 483;. [9]. Chartterjee, R.; Tarafder, G.; Paul S., Groundwater quality assessment of Dhanbad District, District, Jharkhand, India, Bull. Eng. Geol. Environ. 2010, 69:137-141 [10]. Nagarajan, R.; Rajmohan, N.; Mahendran, U.; Senthamilkumar, S., Evaluation of groundater quality and its suitability for drinking and agricultural use in Thanjavur city, Tamil Nadu, India, Environ. Monit. Assess. 2010, 171(1-4289-308 [11]. Srivastava, S. K; Ramanathan, A. L., Geochemical assessment of groundwater quality in vicinity of Bhalswa landfill, Delhi, India, using graphical and multivariate statistical methods. Environmental Geology, 2008, 53, 1509– 1528 [12]. Mondal, N.C., Saxena, V.K. and Singh, V.S, , Environmental Geology, 2005, 48, 149-157 [13]. Trivedy R.K. and Goel P.K, Chemical on biological methods for water pollution studies, Environmental Publications, Karad, 1986 [14]. Raja G. and Venkatesan P, E.Journal of Chemistry, 2010, 7(2), 473-478 [15]. Schroeder HA. Relations between hardness of water and death rates from certain chronic and degenerative diseases in the United States. J Chron disease. 12, 1960, 586-591. [16]. Rao, S.N, National Seminar on Hydrology of Precambrian Terrains and Hard Rock Areas, 1997 129-134 [17]. Chadha, D.K, Hydrogeology Journal, 1999, 7(5), 431-439. Figure 1: Study area location map
  • 4. V. Sunitha. et al. Int. Journal of Engineering Research and Application www.ijera.com ISSN : 2248-9622, Vol. 6, Issue 6, ( Part -5) June 2016, pp.05-08 www.ijera.com 8 | P a g e S. No Village Name pH EC TDS TH mg/L Ca+2 mg/L Cl- mg/L F- mg/L 1 Kottala 7.9 680 435 100 104 32 0.2 2 Gajjalapalli - 1 7.8 590 378 140 88 128 1.5 3 Gajjalapalli - 2 7.4 580 371 160 16 110 6.7 4 Gajjalapalli - 3 7.6 490 314 100 8 92 4 5 Malakavemula 8.2 620 397 80 32 57 1.9 6 Sanevaripalli 8 630 403 140 48 131 1.7 7 Kotareddypalli 7.9 520 333 100 16 67 3.8 8 Vaddekindi tanda 8.2 630 403 100 240 64 2.7 9 Mallepalli 7.1 640 409 180 64 121 2.9 10 Yogi Vemana Reservoir 8 540 346 120 992 74 2.4 11 Dorigallu 7.2 580 371 100 32 88 2.1 12 Eguvapalli 6.9 530 339 140 256 43 0.1 13 Diguvapalli 7.2 610 390 60 32 18 0.4 14 Ambakapalli 6.1 720 461 120 64 28 0.6 15 Nalagondavaripalli- 1 7.9 600 384 80 104 64 0.7 16 Nalagondavaripalli- 2 7.8 580 371 120 88 78 0.2 17 Mallikarjunapuram 8 590 378 100 80 28 0.7 18 Ippatla 7.8 650 416 180 32 160 0.5 19 Chinnakuddala 7.6 670 429 180 40 167 0.5 20 Lingala 8 530 339 180 56 100 0.3 MAX 8.2 720 461 180 992 167 6.7 MIN 6.1 490 314 60 8 18 0.1 MEAN 7.63 599 383 124 119.6 82.5 1.695 STDEV 0.51717 58.6604 37.542 37.0490 215.765 43.5968 1.69627 Table 1: Result of chemical analysis and statistical parameters of groundwater samples collected from the study area during pre monsoon season. S. No Village Name pH EC TDS TH mg/L Ca+2 mg/L Cl- mg/L F- mg/L 1 Kottala 7.6 600 384 80 100 30 0.2 2 Gajjalapalli - 1 7.4 550 352 120 80 120 1.3 3 Gajjalapalli - 2 7.2 500 320 140 16 100 6.6 4 Gajjalapalli - 3 7.2 450 288 80 8 90 3.8 5 Malakavemula 8 560 358 70 30 50 1.6 6 Sanevaripalli 7.8 580 371 130 46 130 1.5 7 Kotareddypalli 7.7 480 307 80 14 60 3.6 8 Vaddekindi tanda 8 560 358 90 220 60 2.5 9 Mallepalli 7 570 365 170 60 120 2.7 10 Yogi Vemana Reservoir 7.8 460 294 100 900 70 2.2 11 Dorigallu 7 500 320 80 30 80 2 12 Eguvapalli 6.6 460 294 130 250 40 0.1 13 Diguvapalli 7 520 333 50 30 16 0.2 14 Ambakapalli 6 640 410 100 60 26 0.3 15 Nalagondavaripalli- 1 7.7 530 339 70 100 60 0.5 16 Nalagondavaripalli- 2 7.4 520 333 100 80 70 0.2 17 Mallikarjunapuram 7.8 460 294 80 70 26 0.5 18 Ippatla 7.6 580 371 160 30 158 0.3 19 Chinnakuddala 7.4 600 384 170 40 160 0.3 20 Lingala 7.8 470 300 160 50 98 0.2 MAX 8 640 410 170 900 160 6.6 MIN 6 450 288 50 8 16 0.1 MEAN 7.4 529.5 338.88 108 110.7 78.2 1.53 STDV 0.50 56.14 35.93 36.93 196.15 43.08 1.68 Table 2: Result of chemical analysis and statistical parameters of groundwater samples collected from the study area during post monsoon season. S.No Parameters ISI 1983 Mean value of parameters under analysis Pre monsoon Post Monsoon 1 PH 6.5-8.5 7.63 7.4 2 EC - 599 529.5 3 TDS 500 383.36 338.88 4 TH 300 124 108 5 Ca+2 75 119.6 110.7 6 Cl- 250 82.5 78.2 7 F- 1.5 1.695 1.53 Table 3: Indian Standards (ISI 1983) for drinking and public health purposes.