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IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________
Volume: 03 Issue: 12 | Dec-2014, Available @ http://www.ijret.org 144
IMPACT OF INDUSTRIES ON GROUND WATER QUALITY BY
COMPARISON BETWEEN HOSHANGABAD (NON INDUSTRIAL
AREA) AND MANDIDEEP (INDUSTRIAL AREA), BHOPAL (INDIA)
Abhishek Mandloi1
1
Student of Department of Structural Engineering, National Institute of Technical Teacher's Training and Research,
Bhopal
Abstract
India is a developing country, so the industrialization is increasing day by day. Industrialization shows the growth of country but
these industries also effects the ground water quality, in a direct manner as well as indirect manner. My case study aim to show
impact of industries on ground water quality by comparison between an industrial (Mandideep) and non-industrial
(Hoshangabad) area. For this, four different source of different locations are selected for analyzing the parameter pH, Total
Hardness, Sulphate,Chloride, Dissolved Oxygen (DO), T.D.S., T.H., T.A ,compared theses result to WHO and ISI standards and
also these parameters compared between both the cities.
Keywords: Ground water quality, Pollution, Lake
-------------------------------------------------------------------***------------------------------------------------------------------
1. INTRODUCTION
Over two third area of Earth covered by water and left one
third taken up by land. Water is in such a very rich
proportion present on our planet but the conservation of this
water bodies in a pure form is the basic and very important
need of whole world.
India is a developing country. Its population around 1.252
billion according to 2013 census, for this population
availability and supply of potable water is very major
challenge for us. In India the major source of drinking water
is running river, lakes and in some rural areas wells and
hand pumps are also the source of drinking water, but due to
rapidly increase in population, industrialization,
urbanization, technology development and access use of
chemicals in agriculture, are the major source of water
pollution. These source dispose waste water directly to
running stream without any treatment thus decrease in
potability of water.
2. STUDY AREA
Mandideep lies between 23°5′40″N 77°31′5″E. Mandideep
is a municipality in Goharganj sub-district of raisen district.
It is an Industrial area near Bhopal at distance 32 km. It has
number of large and small industries some of major
industries are Hindustan Electro Graphite (HEG), Procter &
Gamble, Eicher tractor Ltd. , Lupin laboratries. This
industrial area boasts turnover of Rs. 1700 crore and
revenue of Rs. 1400 crore in the form of various taxes
such as central excise, commercial tax, income-tax, property
tax, etc.
Hoshangabad lies between the parallels of 22°75′N 77°72′E.
In Hoshangabad district, there are two main rivers namely
the Narmada and the Tawa. A very big lake is also at
Pachmarhi, which is one of the main tourist place of the
district. Hoshangabad is a very rich district for agriculture
because of prencese of “Black cotton soil” at many of land
area. It is totally an agricultural area, but only a two industry
(Security Paper Mill Hoshangabad) is situated away to the
city and Vardhman textile industry.
Mandideep has mainly chemical electro graphite dyes,
plastic and rubber Industrial units. Most of these industries
produce waste containing toxic heavy metals along with
hazardous organic and inorganic effluents; these chemicals
contaminate ground water while in Hoshangabad only water
is polluted due to only improper drainage in some regions.
3. MATERIAL AND METHODS
The main objective of surface water quality monitoring is to
assess the existing level of ground water pollution and give
an idea about the impact of industry on natural ground water
sources. On the basis of preliminary survey of the study
area, four numbers of sampling location with different
sources of water were selected in both the cities.
In order to assess the ground water samples quality water
samples were collected from these sampling stations during
financial year 2014.The sampling stations and locations are
given in table-1 and table -2.
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________
Volume: 03 Issue: 12 | Dec-2014, Available @ http://www.ijret.org 145
Table 1: Sampling stations and locations (Mandideep)
Source Location
S1-Tubewell Bisankheda
S2 -Tubewell HEG
S3-Municipal water Indus Township
S4-Handpump Nayapura
Table 2: Sampling stations and locations (Hoshangabad)
Source Location
S1 -Tubewell Vardhman
S2 -Municipal water Rashuliya
S3- Handpump Hanumangarh
S4- Handpump Adamgarh
4. PARAMETERS ANALYZED
Following parameters were analysed during the course of
study
4.1 pH
The hydrogen ion concentration is the indicator of acidity
and alkalinity of any aqueous system. During present
investigation pH was measured with the help of a pH meter
4.2 Turbidity
Turbidity was determined with the help of Nephalo Metric
Turbidity Tube. The results are expressed as Nephalometric
Turbidity Unit (NTU).
4.3 Dissolved Oxygen
Dissolved oxygen was analyzed by Winkler's method with
azide modification following the description given in
APHA.
4.4 Total Dissolved Solids
T.D.S. was measured using the electronic TDS meter (ELE)
and was reported as mg/l or parts per million (ppm).
4.5 Total Alkalinity
T.A. was measured by titrating the water sample with
sulphuric acid of known value of pH, volume and
concentration.
4.6 Total Hardness
T.H. was measured by buffered the water sample to pH 10.1
and taken in to a conical flask and indicator EBT is added to
solution containing calcium and magnesium ions, the color
of the solution turns wine red.
4.7 Sulphate
SO4
2-
was measured first mixed water sample with BaCl2
and then sample is analysis by spectrometer at 420 mm and
sulphate ion determined by standard curve given in APHA
20th edition method 4500E.
4.8 Chloride
Cl-
was measuring by titrating water sample by silver nitrate
solution as per IS 3025 (Part 32).
The water sample were collected in plastic canes of 3 liter
capacity as per standard procedure
5. RESULTS
The average value of chemical parameters during financial
year 2013, are presented in table 3 and table 4. The values
obtained were compared with standard value prescribed by
WHO and ISI-10500-91.
The PH values varied between 6.6 to 7.4 in both the area
and found within the prescribed limit suggested by W.H.O.
T.D.S. values in Mandideep area varied from 121 to 1725
mg/l. It shows that sample S1 and S2 have higher values
than the prescribed limit given by ISI 10500-91 but in
Hoshangabad area T.D.S. value varies 163 to 550mg/l. It
clearly indicate the impact of industry waste on the water
quality in Mandideep area.
Similarly D.O. values.in Mandideep areavaried between 4.9
to 7.1. It shows higher value (sample S1 and S2) than
prescribed limit given by ISI 10500-91 , also in
Hoshangabad (near vardhman factory) area, its little more
than ISI 10500-91.
In the present study the turbidity values in both the areas
varies between 3.4 to 6.2, N.T.U and found within the
prescribed limit
Total alkalinity values for tube well samples taken in both
the area were found to be greater than the prescribed limit
by ISI 10500-91. Total hardness values for tube well
samples were found to be greater than prescribed limit by
ISI 10500-91 in Hoshangabad (near the factory) as well in
Mandideep area.
The Chloride values for tube well samples taken in
Mandideep area were found greater than prescribed limit by
ISI 10500-91, but in Hoshangabad area it is in limit
Prescribed by ISI 10500-91.
The sulphate values in both the area varies from 41.93 to
99.00 mg/l and was found within the prescribed limit.
6. CONCLUSION
This case study clearly shows that the ground water in the
study of area exceeded the prescribed limit of Total
dissolved solids, Total Hardness, Total alkalinity and
chlorides limits prescribed by ISI -10500 (1991) at sampling
station S(1) and S(2) in Mandideeep area while in
Hoshagabad area the value of T.D.S, T.H., T.A., chloride,
sulphate, Turbidity are within limit as prescribed in ISI-
10500(1991).
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
_______________________________________________________________________________________
Volume: 03 Issue: 12 | Dec-2014, Available @ http://www.ijret.org 146
On the basis of experiment carried out it may be stated that
the quality of tube well water is inferior as compared to
Hand pump and Municipal water. It may be due to impact of
industrial and domestic effluents. Such high values will have
negative impacts on the health of Human beings residing in
that area, judiously the corrective measures should be
adopted to prevent increase of Chemical parameter in
ground water in Mandideep area to safe guard public health
while in Hoshangabad has a safe drinking water for public
health without any treatment.
REFERENCES
[1] Tanner, C. C., Clayton, J.S., and Upsdell, M. P.;
Effect of loading rate and planting on treatment of
dairy farm wastewater in constructed II. Removal of
nitrogen and phosphorus. Water Research. 29: 27-34
(1995b).
[2] Tshobanoglous G and Culp, G.L.; Wetland Systems
for Wastewater Treatment: An Engineering
Assessment. US Environmental Protection Agency,
Office of Water Programme Operations, Series
Water EPA 430/9-80-007, Washington DC. (1980).
[3] Gersberg, R.M., Elkins, B.V., Lyon, S.R., and
Goldman, C.R; Role of aquatic plants in wastewater
treatment by artificial wetlands, Water Research, 20:
363-368. (1986).
[4] Iqbal S. A., Khan S.S., Chaghtai S. A. and Irfan
Husain; Assesment of pollution levels of river
Betwa, J. Sci. Res., 6(3): 165 -170 (1984).
[5] WHO, world Health Organisation International
Standard for Drinking Water, Geneva, Swizerland
(1993).
[6] Indian Standard Specification for Drinking Water,
ISI, New Delhi (1991).
Table 3: Ground water quality from the study area ( Mandideep industrial area) with drinking water standard
Table 4: Ground water quality from the study area (Hoshangabad area) with drinking water standards
S.
No
Paremeters S1 S2 S3 S4 W.H.O.1993 ISI 10500-91
Min. Max.
1. PH 6.6 7.1 7.1 7.4 6.7 7.7 6.5-8.5 7.8-5
2. T.D.S 1725 490 100 121 160 1080 1000 500
3. Turbidity 5.1 5.1 3.4 6.2 3.8 8.6 - 10
4. D.O. 4.1 3.5 7.1 3.5 2.7 8.2 - 5.0
5. T.A. 305 550 125 145 140 614 120 200
6. T.H. 721 610 154 209 168 923 500 300
7. Cl-
455.0 190.00 170 125 69.02 477.5 250 250
8. SO4
2-
99.00 53.00 50.79 41.53 39.73 93.39 250 200
S.
No
Paremeters S1 S2 S3 S4 W.H.O.1993 ISI 10500-91
Min. Max.
1. PH 6.5 7.0 6.9 7.6 6.7 7.7 6.5-8.5 7.8-5
2. T.D.S 550 450 163 165 160 1080 1000 500
3. Turbidity 5.0 6.0 5.7 7.5 3.8 8.6 - 10
4. D.O. 5.1 7.1 6.5 4.9 2.7 8.2 - 5.0
5. T.A. 175 155 110 175 140 614 120 200
6. T.H. 345 192 185 190 168 923 500 300
7. Cl-
155.0 100.52 95.01 102.3 69.02 477.5 250 250
8. SO4
2-
51.00 49.20 40.23 41.25 39.73 93.39 250 200

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Impact of industries on ground water quality by comparison between hoshangabad (non industrial area) and mandideep (industrial area), bhopal (india)

  • 1. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________ Volume: 03 Issue: 12 | Dec-2014, Available @ http://www.ijret.org 144 IMPACT OF INDUSTRIES ON GROUND WATER QUALITY BY COMPARISON BETWEEN HOSHANGABAD (NON INDUSTRIAL AREA) AND MANDIDEEP (INDUSTRIAL AREA), BHOPAL (INDIA) Abhishek Mandloi1 1 Student of Department of Structural Engineering, National Institute of Technical Teacher's Training and Research, Bhopal Abstract India is a developing country, so the industrialization is increasing day by day. Industrialization shows the growth of country but these industries also effects the ground water quality, in a direct manner as well as indirect manner. My case study aim to show impact of industries on ground water quality by comparison between an industrial (Mandideep) and non-industrial (Hoshangabad) area. For this, four different source of different locations are selected for analyzing the parameter pH, Total Hardness, Sulphate,Chloride, Dissolved Oxygen (DO), T.D.S., T.H., T.A ,compared theses result to WHO and ISI standards and also these parameters compared between both the cities. Keywords: Ground water quality, Pollution, Lake -------------------------------------------------------------------***------------------------------------------------------------------ 1. INTRODUCTION Over two third area of Earth covered by water and left one third taken up by land. Water is in such a very rich proportion present on our planet but the conservation of this water bodies in a pure form is the basic and very important need of whole world. India is a developing country. Its population around 1.252 billion according to 2013 census, for this population availability and supply of potable water is very major challenge for us. In India the major source of drinking water is running river, lakes and in some rural areas wells and hand pumps are also the source of drinking water, but due to rapidly increase in population, industrialization, urbanization, technology development and access use of chemicals in agriculture, are the major source of water pollution. These source dispose waste water directly to running stream without any treatment thus decrease in potability of water. 2. STUDY AREA Mandideep lies between 23°5′40″N 77°31′5″E. Mandideep is a municipality in Goharganj sub-district of raisen district. It is an Industrial area near Bhopal at distance 32 km. It has number of large and small industries some of major industries are Hindustan Electro Graphite (HEG), Procter & Gamble, Eicher tractor Ltd. , Lupin laboratries. This industrial area boasts turnover of Rs. 1700 crore and revenue of Rs. 1400 crore in the form of various taxes such as central excise, commercial tax, income-tax, property tax, etc. Hoshangabad lies between the parallels of 22°75′N 77°72′E. In Hoshangabad district, there are two main rivers namely the Narmada and the Tawa. A very big lake is also at Pachmarhi, which is one of the main tourist place of the district. Hoshangabad is a very rich district for agriculture because of prencese of “Black cotton soil” at many of land area. It is totally an agricultural area, but only a two industry (Security Paper Mill Hoshangabad) is situated away to the city and Vardhman textile industry. Mandideep has mainly chemical electro graphite dyes, plastic and rubber Industrial units. Most of these industries produce waste containing toxic heavy metals along with hazardous organic and inorganic effluents; these chemicals contaminate ground water while in Hoshangabad only water is polluted due to only improper drainage in some regions. 3. MATERIAL AND METHODS The main objective of surface water quality monitoring is to assess the existing level of ground water pollution and give an idea about the impact of industry on natural ground water sources. On the basis of preliminary survey of the study area, four numbers of sampling location with different sources of water were selected in both the cities. In order to assess the ground water samples quality water samples were collected from these sampling stations during financial year 2014.The sampling stations and locations are given in table-1 and table -2.
  • 2. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________ Volume: 03 Issue: 12 | Dec-2014, Available @ http://www.ijret.org 145 Table 1: Sampling stations and locations (Mandideep) Source Location S1-Tubewell Bisankheda S2 -Tubewell HEG S3-Municipal water Indus Township S4-Handpump Nayapura Table 2: Sampling stations and locations (Hoshangabad) Source Location S1 -Tubewell Vardhman S2 -Municipal water Rashuliya S3- Handpump Hanumangarh S4- Handpump Adamgarh 4. PARAMETERS ANALYZED Following parameters were analysed during the course of study 4.1 pH The hydrogen ion concentration is the indicator of acidity and alkalinity of any aqueous system. During present investigation pH was measured with the help of a pH meter 4.2 Turbidity Turbidity was determined with the help of Nephalo Metric Turbidity Tube. The results are expressed as Nephalometric Turbidity Unit (NTU). 4.3 Dissolved Oxygen Dissolved oxygen was analyzed by Winkler's method with azide modification following the description given in APHA. 4.4 Total Dissolved Solids T.D.S. was measured using the electronic TDS meter (ELE) and was reported as mg/l or parts per million (ppm). 4.5 Total Alkalinity T.A. was measured by titrating the water sample with sulphuric acid of known value of pH, volume and concentration. 4.6 Total Hardness T.H. was measured by buffered the water sample to pH 10.1 and taken in to a conical flask and indicator EBT is added to solution containing calcium and magnesium ions, the color of the solution turns wine red. 4.7 Sulphate SO4 2- was measured first mixed water sample with BaCl2 and then sample is analysis by spectrometer at 420 mm and sulphate ion determined by standard curve given in APHA 20th edition method 4500E. 4.8 Chloride Cl- was measuring by titrating water sample by silver nitrate solution as per IS 3025 (Part 32). The water sample were collected in plastic canes of 3 liter capacity as per standard procedure 5. RESULTS The average value of chemical parameters during financial year 2013, are presented in table 3 and table 4. The values obtained were compared with standard value prescribed by WHO and ISI-10500-91. The PH values varied between 6.6 to 7.4 in both the area and found within the prescribed limit suggested by W.H.O. T.D.S. values in Mandideep area varied from 121 to 1725 mg/l. It shows that sample S1 and S2 have higher values than the prescribed limit given by ISI 10500-91 but in Hoshangabad area T.D.S. value varies 163 to 550mg/l. It clearly indicate the impact of industry waste on the water quality in Mandideep area. Similarly D.O. values.in Mandideep areavaried between 4.9 to 7.1. It shows higher value (sample S1 and S2) than prescribed limit given by ISI 10500-91 , also in Hoshangabad (near vardhman factory) area, its little more than ISI 10500-91. In the present study the turbidity values in both the areas varies between 3.4 to 6.2, N.T.U and found within the prescribed limit Total alkalinity values for tube well samples taken in both the area were found to be greater than the prescribed limit by ISI 10500-91. Total hardness values for tube well samples were found to be greater than prescribed limit by ISI 10500-91 in Hoshangabad (near the factory) as well in Mandideep area. The Chloride values for tube well samples taken in Mandideep area were found greater than prescribed limit by ISI 10500-91, but in Hoshangabad area it is in limit Prescribed by ISI 10500-91. The sulphate values in both the area varies from 41.93 to 99.00 mg/l and was found within the prescribed limit. 6. CONCLUSION This case study clearly shows that the ground water in the study of area exceeded the prescribed limit of Total dissolved solids, Total Hardness, Total alkalinity and chlorides limits prescribed by ISI -10500 (1991) at sampling station S(1) and S(2) in Mandideeep area while in Hoshagabad area the value of T.D.S, T.H., T.A., chloride, sulphate, Turbidity are within limit as prescribed in ISI- 10500(1991).
  • 3. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 _______________________________________________________________________________________ Volume: 03 Issue: 12 | Dec-2014, Available @ http://www.ijret.org 146 On the basis of experiment carried out it may be stated that the quality of tube well water is inferior as compared to Hand pump and Municipal water. It may be due to impact of industrial and domestic effluents. Such high values will have negative impacts on the health of Human beings residing in that area, judiously the corrective measures should be adopted to prevent increase of Chemical parameter in ground water in Mandideep area to safe guard public health while in Hoshangabad has a safe drinking water for public health without any treatment. REFERENCES [1] Tanner, C. C., Clayton, J.S., and Upsdell, M. P.; Effect of loading rate and planting on treatment of dairy farm wastewater in constructed II. Removal of nitrogen and phosphorus. Water Research. 29: 27-34 (1995b). [2] Tshobanoglous G and Culp, G.L.; Wetland Systems for Wastewater Treatment: An Engineering Assessment. US Environmental Protection Agency, Office of Water Programme Operations, Series Water EPA 430/9-80-007, Washington DC. (1980). [3] Gersberg, R.M., Elkins, B.V., Lyon, S.R., and Goldman, C.R; Role of aquatic plants in wastewater treatment by artificial wetlands, Water Research, 20: 363-368. (1986). [4] Iqbal S. A., Khan S.S., Chaghtai S. A. and Irfan Husain; Assesment of pollution levels of river Betwa, J. Sci. Res., 6(3): 165 -170 (1984). [5] WHO, world Health Organisation International Standard for Drinking Water, Geneva, Swizerland (1993). [6] Indian Standard Specification for Drinking Water, ISI, New Delhi (1991). Table 3: Ground water quality from the study area ( Mandideep industrial area) with drinking water standard Table 4: Ground water quality from the study area (Hoshangabad area) with drinking water standards S. No Paremeters S1 S2 S3 S4 W.H.O.1993 ISI 10500-91 Min. Max. 1. PH 6.6 7.1 7.1 7.4 6.7 7.7 6.5-8.5 7.8-5 2. T.D.S 1725 490 100 121 160 1080 1000 500 3. Turbidity 5.1 5.1 3.4 6.2 3.8 8.6 - 10 4. D.O. 4.1 3.5 7.1 3.5 2.7 8.2 - 5.0 5. T.A. 305 550 125 145 140 614 120 200 6. T.H. 721 610 154 209 168 923 500 300 7. Cl- 455.0 190.00 170 125 69.02 477.5 250 250 8. SO4 2- 99.00 53.00 50.79 41.53 39.73 93.39 250 200 S. No Paremeters S1 S2 S3 S4 W.H.O.1993 ISI 10500-91 Min. Max. 1. PH 6.5 7.0 6.9 7.6 6.7 7.7 6.5-8.5 7.8-5 2. T.D.S 550 450 163 165 160 1080 1000 500 3. Turbidity 5.0 6.0 5.7 7.5 3.8 8.6 - 10 4. D.O. 5.1 7.1 6.5 4.9 2.7 8.2 - 5.0 5. T.A. 175 155 110 175 140 614 120 200 6. T.H. 345 192 185 190 168 923 500 300 7. Cl- 155.0 100.52 95.01 102.3 69.02 477.5 250 250 8. SO4 2- 51.00 49.20 40.23 41.25 39.73 93.39 250 200