Ijraset Journal For Research in Applied Science and Engineering Technology
Authors: Bharat Kumar Dhangar, Vasundhara Dhangar, KM Sharma
DOI Link: https://doi.org/10.22214/ijraset.2024.59749
Certificate: View Certificate
Water is one of the earth most important resources that use for Human life and it,s quality is totally depend on geological environment. Chambal is an important river in Mandshour M.P. Hence made to WQI and Pollution or change in the quality of water. The Quality Index (WQI) Is an important tool to determine the drinking water quality in rural, urban, agriculture and industrial area. WQI follows four step parameter selection, sub-indices, establishing weight, and final index aggregation. Assessment of WQI of River Chambal includes physic-chemical parameter viz. Biological Oxygen Demand, Dissolved Oxygen, PH, Total Hardness, Total alkaline ions and solids thate indicate the extent of pollution.
I. INTRODUCTION
Mandshour district is located on border of Malwa region on Madhya Pradesh between 24.071955 North latitude and 75.069404 East longitude. Total geographical area of district is 50 sq. km. Average maximum temperature is 104?F and minimum 55?F. Mandshour is also famous for Pashupatinath Templea hindu situated on the bank of the shivana river.
River Chambal in Gandhi sagar sanctuary .The Gandhi sagar dam is the first of the 4 dams built on the Chambal river.
All metabolic reactions occur in the water Water, the most vital component, is necessary for the continuity of life . The water quality is affected by geological formations, anthropogenic activities, current trends of urbanization, over-exploitation of resources and exorbitantly increasing population [1] River water pollution is challenging issue in India due to continuous urbanization and rapid industrialization for sustainable development [2]. Most of the industries are disposing off their waste directly to the nearby stream without making any treatment and violating the provisions for standard laid out for the same [3].On national and state levels several policies and regulations like Water Act, 1974 (Prevention and Control of Pollution) to regulate pollution discharges and restore water quality of aquatic resources including the prescription of monitoring activities. Now a day’s water quality assessment as major concern as it is getting deteriorated by human activities [4] .
The water quality is affected by geological formations, anthropogenic activities, current trends of urbanization, over-exploitation of resources and exorbitantly increasing population [5].
The water quality of river can predict by using the Water Quality Index. Basically a WQI attempts to provide a mechanism for presenting a cumulatively derived, numerical expression defining a certain level of water quality [6].It is introduced as a mathematical instrument to convert the water quality dataset into a single number which represents the water quality and biases of individual water quality experts [7]
II. MATERIALS AND METHODS
III. WATER QUALITY CRITERIA FOR IRRIGATION
The WQI is the one of the most widely used of all existing water quality procedures [17].Therefore, WQI is simplified way of representing water quality information The WQI has been calculated by using the standards of drinking water quality recommended by the World Health Organization (WHO), Indian Council of Medical Research (ICMR, 1975) and Bureau of Indian Standards (BIS) has been used for the calculation of WQI of the water body. [18][19] .Quality of water is an important aspect in any appraisal of salinity or alkalinity conditions in an irrigated area. Good soil and water management practices result in good quality of water are ideal for agriculture.
A. Sodium Absorption Ratio(SAR)
SAR is an vital parameter given by Richard in 1954[21] .The basic concept behind the SAR is to find out the soil alkalinity of water used for irrigation purposes[22]
Table:-1
Classification of Water samples on the basis of basis Statistical Analysis
Statistical Analysis Parameters |
Categories |
Range |
SodiumAbsorption Ratio(SAR) |
Excellent Good Fair Poor |
0-10 10-18 18-26 >26 |
ChloroAlkanine Indices(CAI) |
Base Exchange Reaction
Cation Exchange Reaction |
Negative Value Positive Value |
Sodium Percentage(%Na) |
Excellent Good Permissible |
0-20 20-40 40-60 |
Table:-2
Interpretation of Langelier Saturated Index (LSI) Test Result
S.No. |
LSI Index |
Appearance |
Water Condition Issues required |
1 |
-4.00 |
Very severe corrosion |
Conditioning required |
2 |
-3.00 |
severe corrosion |
Conditioning usually suggested |
3 |
-2.00 |
Moderate corrosion |
Some conditioning is suggested |
4 |
-1.00 |
Mild corrosion |
Required some conditioning |
5 |
-0.50 |
Slight corrosion |
May need some conditioning |
6 |
0.00 |
Balanced |
Conditioning not suggested |
7 |
0.50 |
Faint Scale Coating |
Conditioning not suggested |
8 |
1.00 |
Slight Scale Coating |
Some visual appearance shown |
9 |
2.00 |
Mild Scale Coating |
Should consider some conditioning |
10 |
3.00 |
Moderate Scale Coating |
Should use some conditioning |
11 |
4.00 |
Severe Scale Coating |
Usually conditioning required |
Table:-3
Statistical Analysis of Various Water Sample Readings Water Quality during Year -2019-2020
|
Characteristic |
Unit |
April |
May |
June |
July |
Aug. |
Sept. |
Oct. |
Nov. |
Dec. |
Jan. |
Feb |
1 |
Date of Sampling |
- |
10.4.19 |
10.5.19 |
21.6.19 |
5.7.19 |
13.8.19 |
10.9.19 |
16.10.19 |
3.11.19 |
12.12.19 |
30.1.20 |
27.2.20 |
2 |
Appearance |
- |
Clear |
Clear |
Clear |
Clear |
Clear |
Clear |
Clear |
Clear |
Clear |
Clear |
Clear |
3 |
Temperature |
oC |
34 |
38 |
30 |
23 |
22 |
22 |
24 |
25 |
22 |
23 |
-- |
4 |
Turbidity |
NTU |
3.8 |
8.3 |
6.4 |
7.6 |
9.4 |
9.6 |
4.6 |
7.6 |
4.3 |
3.1 |
3.8 |
5 |
Colour |
PCS |
Colourless |
Colourless |
Colourless |
Colourless |
Colourless |
Colourless |
Colourless |
Colourless |
Colourless |
Colourle |
Colourles |
6 |
Odour |
T. No |
Odourless |
Odourless |
Odourless |
Odourless |
Odourless |
Odourless |
Odourless |
Odourless |
Odourless |
Odourles |
Odourless |
7 |
pH |
pH Unit |
7.78 |
7.86 |
7.96 |
7.77 |
7.88 |
7.78 |
7.94 |
7.84 |
7.86 |
7.86 |
7.84 |
8 |
Sp. Conductivity |
µMhos/cm. |
310 |
494 |
348 |
334 |
282 |
288 |
274 |
282 |
252 |
254 |
294 |
9 |
T. Solids |
mg/1 |
226 |
354 |
244 |
240 |
224 |
228 |
212 |
208 |
194 |
226 |
238 |
10 |
D. Solids |
mg/1 |
210 |
342 |
226 |
226 |
206 |
208 |
198 |
198 |
182 |
208 |
222 |
11 |
S. Solids |
mg/1 |
16 |
12 |
18 |
14 |
18 |
20 |
14 |
10 |
12 |
18 |
16 |
12 |
Amm. Nitrogen |
mg/1 |
0.412 |
0.422 |
0.348 |
0.426 |
0.284 |
0.288 |
0.102 |
0.126 |
0.122 |
0.13 |
0.16 |
13 |
Nitrite Nitrogen |
mg/1 |
0.058 |
0.008 |
0.006 |
0.007 |
0.004 |
0.006 |
0.001 |
0.001 |
0.001 |
0.0018 |
0.004 |
14 |
Nitrate Nitrogen |
mg/1 |
0.82 |
1.236 |
0.98 |
0.818 |
0.862 |
0.878 |
0.884 |
0.894 |
0.686 |
0.589 |
1.32 |
15 |
Phosphate (PO4) |
mg/1 |
BDL |
BDL |
BDL |
BDL |
0.03 |
0.03 |
0.026 |
0.028 |
BDL |
BDL |
BDL |
16 |
Chloride |
mg/1 |
42 |
72 |
54 |
25 |
38 |
42 |
28 |
34 |
32 |
34 |
46 |
17 |
Sulphate (SO4) |
mg/1 |
26.2 |
28.2 |
40.2 |
26.26 |
24.16 |
30.18 |
16.8 |
18.6 |
13.2 |
13.8 |
41.2 |
18 |
T. Alkalinity |
mg/1 |
128 |
138 |
150 |
110 |
116 |
126 |
104 |
110 |
108 |
120 |
198 |
19 |
T. Hardness |
mg/1 |
160 |
180 |
188 |
148 |
172 |
178 |
142 |
164 |
204 |
240 |
216 |
20 |
CalciumHardness |
mg/1 |
82 |
110 |
100 |
90 |
110 |
114 |
94 |
102 |
120 |
128 |
124 |
21 |
Magnesium H. |
mg/1 |
78 |
70 |
88 |
58 |
62 |
64 |
48 |
62 |
84 |
112 |
92 |
22 |
D. Oxygen |
mg/1 |
7 |
7.2 |
7.4 |
7 |
7 |
7 |
7.4 |
7 |
7.1 |
7.3 |
7.2 |
23 |
B.O.D. |
mg/1 |
2.4 |
2.6 |
2.4 |
2 |
2.4 |
2.2 |
2 |
2 |
2 |
2 |
2 |
24 |
C.O.D. |
mg/1 |
18 |
10 |
19 |
12 |
14 |
18 |
10 |
10 |
10 |
12 |
14 |
25 |
Sodium |
mg/1 |
30 |
30.2 |
48.2 |
21.4 |
19.4 |
22.2 |
12.2 |
13.2 |
11.4 |
12.4 |
45.4 |
26 |
Potassium |
mg/1 |
1 |
1 |
1.8 |
1.6 |
1 |
1 |
0.8 |
1 |
1 |
1.1 |
1.2 |
27 |
T. Coliform |
MPN/100m |
58 |
94 |
58 |
49 |
63 |
63 |
47 |
49 |
49 |
47 |
49 |
28 |
F. Coliform |
MPN/100m |
8.2 |
6 |
9.1 |
4 |
6 |
6 |
1.8 |
1.8 |
4 |
1.8 |
4 |
29 |
T.K.N. |
mg/1 |
-- |
-- |
-- |
-- |
-- |
2.8 |
3.36 |
3.36 |
3.36 |
2.8 |
3.36 |
|
CATEGORY |
|
B |
B |
B |
A |
B |
B |
A |
A |
A |
A |
A |
Source:- MADHYA PRADESH POLLUTION CONTROL BOARD ,BHOPAL
IV. ACKNOWLEDGEMENT
We are thankful to Central Laboratory MADHYA PRADESH POLLUTION CONTROL BOARD Bhopal for providing data so that we can interpret readings into results The main objective of M.P. Pollution Control Board is to maintain water, air and soil in healthy and usable condition for various and constantly keeping watch on environmental activities in the state to attain the objectives
Under the Gandhi Sagar Dam project, water in Neemuch and Mandshour districts is used for agriculture and drinking water. The suitability of water for irrigation is evaluated based on Sodium Absorption Ratio, Chloro alkaline indices I, % Na, and salinity hazards. Most of the samples fall in the suitable range for irrigation purpose based on Sodium Absorption Ratio, Chloro alkaline indices, % Na and KR values, but very few samples that are exceeding the permissible limits. These variations are observed to be in different kind of geological areas and different anthropogenic activities were carried in the study area. This study will be helpful in sustainable development of water sources in Neemuch and Mandshour .
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Guru (2003), Evaluation of water quality in Tadepalli Mandal of Guntur [35] www.water-research.net [36] Indian Council of Medical Research (ICMR), New Delhi, India [37] WHO, International Standards for Drinking Water, world health Organization, Geneva, 1971 [38] www.cwejounal.org [39] Jothivenkatachalam K, Nithya A and Chandra Mohan S. (2010), Rasayan J Chem, 3(4), 649-654 [40] R.C. Gupta.A. K.Gupta and R.k. Shrivastava, “Assessment of water quality status of Holy River Kshipra using water quality index”, Journal of Indian Water resources society vol.32, no.01-2, 2012 [41] W. R.Ott, Water Quality Indices: A Survey of Indices Used In the United States, Epa-600/4-78- 005. Washington, Dc: Us Environmental Protection Agency, pp. 128, 1978 [42] S.Kalavathy , R. Sharma T., S. K. P., “Water quality index of river Cauvery in Tiruchirappalli District, Tamil Nadu”, Arch. Environ. Sci.Vol. 5, pp. 55-61, 2011 [43] Raju N. Janardhana (2007), Hydrogeo chemical parameters for assessment of ground water quality in the upper Gunjanaeru River basin, Cuddapah, District, Andhra Pradesh, South India, Environmental Geology, 52 PP 1067-1074. [44] Richard L.A. (1954), Diagnosis and improvement of Saline and Alkali soils, Agric. handbook 60, USDA,Washington D.C., PP 160 [45] Kumaresan M. and Riyazuddin P. (2006), Major ion chemistry of environmental samples around sub-urban of Chennai City, Current Science, 91(12), PP 1668- 1677. | [46] Schoeller H. (1967), Geochemistry of ground water. An international guide for research and practice, UNESCO,
Copyright © 2024 Bharat Kumar Dhangar, Vasundhara Dhangar, KM Sharma. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
Paper Id : IJRASET59749
Publish Date : 2024-04-02
ISSN : 2321-9653
Publisher Name : IJRASET
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