Physico-chemical studies on ground water qualities of some areas of Imphal East district of Manipur during post-monsoon – 3rd phase

 

Nandababu Singh Laishram

Department of Chemistry, D.M. College of Science, Imphal – 795001 Manipur, India

*Corresponding Author E-mail: l.nandababu@yahoo.com

 

 

ABSTRACT:

Fifteen ground water samples ( S-1 to S-15) were collected from different locations (sites) of Imphal East district of Manipur during post-monsoon of 2014. They were analyzed for various physico-chemical parameters such as temperature, pH, TDS (total dissolved solids), electrical conductivity (EC), total alkalinity (TA) (and hence CO32- and HCO3-), total hardness(TH), Ca2+, Mg2+, Na+, K+ and Cl-. In case of S-1 (Keirao Khunou(1), near paddy field), most of the parameters have their values far above the acceptable limits of BIS standard for drinking water and hence it is unfit for drinking and other domestic purposes. But, the ground waters (S-2 to S-15) are fit for drinking and other domestic purposes in absence of alternate sources. However, some suitable treatments are necessary so as to keep the values of total alkalinity (for S-2 to S-15), total hardness (for S-2 to S-6, S-8 to S-9, S-12 and S-15) and Mg2+ (for S-1, S-4 and S-6) below the acceptable limits of BIS standard for drinking water. Again ground waters (S-1 to S-15) are found to be fit for irrigation purpose. Further, correlation co-efficient data indicate the presence of NaCl and KCl salts in such ground waters and high values of TDS are mainly due to presence of NaCl and KCl.

 

KEYWORDS: Physico-chemical parameters, post-monsoon, drinking, irrigation, BIS and correlation co-efficient.

 

 


INTRODUCTION:

With the population growth all over the world, rate of urbanization also increases. As a result of it quantity of surface water bodies decrease day by day due to encroachment for construction of houses, buildings, commercial areas, industrial areas etc. This leads to the more demand for ground water for human consumption, irrigation, industrial and many other purposes.

 

Ground water is about 0.6% of the total global water resources and out of this only 0.3% is extractable economically1. However such ground waters are not always safe for drinking, other domestic, irrigation and industrial purposes. It is, therefore, necessary to monitor the ground water qualities from time to time just like that of regular monitoring of surface water qualities. With a view to this objective many researchers, all over the world had carried out extensive researches on ground water qualities so as to examine whether such ground waters are fit for human consumption, irrigation and many other purposes2-6.In many states of India also, many researchers had carried out extensive researches on ground water qualities in addition to regular monitoring of surface water qualities so as to examine whether such ground waters as well as surface waters are fit for human consumption mainly, other domestic and irrigation purposes7-13.

               

The present aim of this research work is to carry out physico-chemical studies on ground water qualities of some areas of Imphal East district of Manipur during post-monsoon of 2014. This research work is in continuation of my former research work on ground water qualities of some  areas of Imphal West district of Manipur14. 

 

MATERIALS AND METHODS:

All the chemicals were of AR grade and were used as received. Fifteen ground water samples were collected from hand pumps of different locations of Imphal East district during post-monsoon period (November) of 2014. They were collected in well sterilized polythene bottles of one litre capacity each. Guidelines of sampling and preservation were strictly followed15. The fifteen samples were analyzed for physico-chemical parameters such as temperature, pH, TDS (total dissolved solids), electrical conductivity(EC), total alkalinity (TA), CO32-, HCO3-, total hardness (TH), Ca2+, Mg2+, Na+, K+ and Cl-. The geographical locations (both longitudes and latitudes) of different sampling sites, were measured with the help of a GPS instrument and they are shown in table-1 given below:

 


 

Table-1:  Locations (with geographical positions) of fifteen sampling sites

Sample code no. (with source)

Sampling sites (locations)

Longitude

Latitude

S-1

(Hand pump)

Keirao Khunou (1)

( near paddy field)

93058/57.35//E

24044/54.60//N

S-2

(Hand pump)

Keirao Khunou (2)

(Near foothill)

93059/12.02//E

24044/50.70//N

S-3

(Hand pump)

Laipharok(Yaipharok) Maring(1)

(near foothill)

93059/57.53//E

24044/28.58//N

S-4

(Hand pump)

Laipharok (Yaipharok) Maring tampak (2) (near foothill)

94000/11.59//E

24044/29.87//N

S-5

(Hand pump)

Keirao Wangkhem Bazar

94000/23.62//E

24043/55.68//N

S-6

(Hand pump)

Keirao Wangkhem Maning Leikai

94000/30.35//E

24044/4.09//N

S-7

(Hand pump)

Keirao Wangkhem Lairembi Leikai

94000/37.16//E

24044/00.32//N

S-8

(Hand pump)

Ngarian Mamang Leikai

94001/37.80//E

24042/46.11//N

S-9

(Hand pump)

Ngarian Maning Leikai

94001/34.68//E

24042/57.43//N

S-10

(Hand pump)

Huikap Makha Leikai(1)

(near foothill)

94001/48.16//E

24043/04.68//N

S-11

(Hand pump)

Huikap Makha Leikai (2)

(Near foothill)

94001/48.10//E

24043/10.43//N

S-12

(Hand pump)

Huikap Makha Leikai(3)

94001/45.00//E

24043/16.76//N

S-13

(Hand pump)

Uchol Makha Leikai

94002/10.08//E

24044/05.63//N

S-14

(Hand pump)

Uchol Mayai Leikai

94002/09.50//E

24044/11.50//N

S-15

(Hand pump)

Uchol Awang Leikai

(near foothill)

94002/07.14//E

24044/19.35//N

 


 

Parameters like temperature, pH, TDS and electrical conductivity were measured during the time of sampling of each sample while remaining parameters such as total alkalinity, total hardness, Ca2+ and Cl- were determined in departmental research laboratory using standard methods15. Further values of parameters like CO32- and HCO3- were calculated from corresponding total alkalinity values while values of Mg2+ for different samples were calculated from differences of total hardness and calcium hardness of corresponding samples. However, values of Na+ and K+ were determined using a flame photometer. Brief methods and equipments used for determinations and measurements of various physico-chemical parameters of different ground water samples, are detailed in table-2 given below:

 

 

 


Table-2 : Instruments and methods used for measurement / determination of physico-chemical parameters of ground water samples

Physico-chemical paramaters measured / determined

Instruments and methods used

Temperature

TDS Meter (TDS-3) (TDS/Temp.) (HIMEDIA, India)

pH

pHep® Pocket-sized pH Meter (HI98107) (HANNA Instruments, Romania)

TDS (Total dissolved solids)

TDS Meter (TDS-3) (TDS/Temp.) (HIMEDIA, India)

Electrical conductivity (EC)

Conductivity Tester (Dist 3: HI 98303) (HANNA Instruments, Romania)

Total alkalinity (TA)

Titrimetric  method with standard HCI solution using phenolphthalein and methyl orange indicators

CO32- and HCO3-

By calculation method from total alkalinity values

Total hardness (TH)

EDTA titrimetric method (using Eriochrome Black T Indicator)

Calcium (Ca2+)

EDTA titrimetric method (using Murexide indicator)

Magnesium (Mg2+)

By calculation method

Sodium (Na+) and Potassium (K+)

Flame Photometer 128 (Systronics, India)

Chloride (Cl-)

Argentometric titrimetric method (Using K2CrO4 indicator solution)


 

 

Values of parameters such as RSC (residual sodium carbonate) and SAR (sodium adsorption ratio) for the fifteen ground water samples, were calculated using the following relationships16-17:

 

RSC= (CO32-+HCO3-)-(Ca2++Mg2+)

concentrations were expressed in milli-equivalents / litre (meq/L).

 

RESULTS AND DISCUSSION:

All the fifteen (15) ground water samples are found to be colourless and odourless. Values of different physico-chemical parameters for fifteen ground water samples (S-1 to S-15), are shown in table- 3 given below:


 

Table-3: Values of physico-chemical parameters of ground water samples from different sampling sites

Sample code no.

Temper-ature (oC)

pH

TDS

(mg/L)

Electrical

Conducti-vity

(EC) (µS/cm)

Total alkalinity

(TA)

(as CaCO3) (mg/L)

HCO3-

(mg/L)

Total hardness

(TH)

(as CaCO3)

(mg/L)

Ca2+

(mg/L)

Mg2+

(mg/L)

Na+

(mg/L)

K+

(mg/L)

Cl-

(mg/L)

S-1

24

7.4

1030

2346

260

317.2

242

44.1

32.1

338.9

2.2

632.4

S-2

24.9

7.5

259

554

310

378.2

220

43.3

27.2

44.1

1

4.3

S-3

25.1

7.4

281

597

310

378.2

210

36.1

29.2

54.3

1.1

5.7

S-4

22.9

7.3

255

554

300

366

236

42.5

31.6

39

1.1

7.1

S-5

23.6

7.3

272

569

305

372.1

230

44.9

28.7

43.6

1.1

5.7

S-6

23.1

7.3

256

538

300

366

228

40.1

31.1

39.3

1.1

4.3

S-7

23.5

7.6

317

664

360

439.2

76

12.8

10.7

115.4

1.2

7.1

S-8

23.1

7.4

256

546

295

359.9

216

44.9

25.3

43.2

1.4

5.7

S-9

22.3

7.3

225

494

270

329.4

218

48.1

23.8

31.7

0.9

5.7

S-10

23.4

7.4

247

526

260

317.2

128

27.3

14.6

70.1

1.3

8.5

S-11

21.8

7.3

231

485

260

317.2

174

35.3

20.9

45.5

1.7

7.1

S-12

22

7.4

232

492

275

335.5

204

43.3

23.3

37.5

1.2

4.3

S-13

22

7.4

225

494

260

317.2

136

24.8

18

39.7

0.9

4.3

S-14

21.8

7.7

237

522

275

335.5

80

18.4

8.3

58.7

1.5

4.3

S-15

22

7.5

232

504

275

335.5

216

48.9

22.8

24

0.9

5.7

 

 


Based on the above experimental results of various physico-chemical parameters of different ground water samples, the following discussion has been made:

 

Temperature:

The temperature of fifteen ground water samples (S-1 to S-15) are in the range 21.8-25.10C (table-3). S-3 has the highest temperature (25.10C) while those of S-11 and S-14 are the least (21.80C).

pH Values :

The pH values for the ground water samples (S-1 to S-15) range from 7.3 to 7.7 (table-3). S-14 has highest pH value (7.7) while that of S-4 to S-6, S-9 and S-11 are the least one (7.3).

 

All the pH values for the fifteen ground water samples are within the acceptable limits (6.5-8.5) of BIS standard for drinking water as well as that of WHO18-19.

TDS (Total dissolved solids):

The TDS values for the ground water samples (S-1 to S-15) are in the range 225-1030 mg/L (table-3). S-1 has highest TDS value (1030 mg/L) while that of S-9 and S-13 are the lowest (225 mg/L). Except S-1, remaining fourteen ground water samples (S-2 to S-15) have their TDS values below the acceptable limit (500 mg/L) of BIS standard for drinking water 18. Except S-1, TDS values for S-2 to S-15 are below 1000 mg/L and hence they are suitable for other domestic purposes20.

 

Electrical conductivity (EC):

The electrical conductivity values for the fifteen ground water samples (S-1 to S-15) range from 485-2346 µS/cm (table-3). S-1 has the highest value (2346 µS /cm) while S-11 has the least value (485 µS /cm).

 

Total alkalinity (TA):

The values of total alkalinity for the fifteen ground water samples (S-1 to S-15) range from 260 mg/L to 360 mg/L (table-3). S-7 has the highest value (360 mg/L) of total alkalinity while those of S-1, S-10, S-11 and S-13 have the lowest value (260mg/L). All the total alkalinity values for the fifteen ground water samples are above the acceptable limit (200 mg/L) but below the permissible limit (600 mg/L) of BIS standard for drinking water18.

 

CO32- and HCO-3:

The phenolphthalein alkalinity (P-alkalinity) values for the fifteen ground water samples are found to be zero and hence CO32- is almost absent or beyond detectable limit. Therefore, total alkalinity for different ground water samples is due to the presence of HCO-3ions only. The concentrations of HCO3- for different ground waters range from 317.2 mg/L to 439.2 mg/L (table-3). S-7 has highest value while that of S-1, S-10, S-11 and S-13 is the least one.

 

Total hardness (TH):

The values of total hardness for the fifteen ground water samples (S-1 to S-15) are in the range 76-242 mg/L (table -3). S-1 has highest value of total hardness (242 mg/L) while that of S-7 is the lowest one (76 mg/L). The total hardness values for S-7, S-10, S-11, S-13 and S-14 are below the acceptable limit (200 mg/L) while that of remaining samples- S-1 to S-6, S-8 to S-9, S-12 and S-15 have their values below the permissible limit (600 mg/L) of BIS standard for drinking water18. Further, it is clearly seen from table-3 that S-7, S-10, S-13 and S-14 belong to moderately hard water category (75-150 mg/L) while remaining ground water samples (S-1 to S-6, S-8 to S-9, S-11 to S-12 and S-15 belong to hard water category (150-300 mg/L)20.

 

 

 

Calcium (Ca2+):

Concentrations of Ca2+ for the fifteen ground water samples (S-1 to S-15) are in the range 12.8-48.9 mg/L (table-3). S-7 has the lowest concentration of Ca2+ (12.8 mg/L) while that of S-15 is the highest (48.9 mg/L). All the concentrations of Ca2+ for the fifteen ground water samples, are below the acceptable limit (75 mg/L) of BIS standard for drinking water18.

 

Magnesium (Mg2+):

Regarding magnesium contents for the fifteen ground water samples (S-1 to S-15), the concentration values range from 8.3 mg/L to 32.1 mg/L (table-3). S-14 has the lowest concentration of Mg2+ (8.3 mg/L) while S-1has highest concentration of Mg2+(32.1 mg/L). Ground waters represented by S-2 to S-3, S-5 and S-7 to S-15 have their concentrations of Mg2+ below the acceptable limit (30mg/L) while those of S-1, S-4 and S-6, are below the permissible limit (100mg/L) of BIS standard for drinking water18.

 

Sodium (Na+):

The concentrations of sodium for the fifteen ground water samples (S-1 to S-15) are in the range 24-338.9 mg/L (table-3). S-1 has highest concentration of Na+ (338.9 mg/L) while S-15 has lowest concentration of Na+ (24 mg/L). Except S-1, other remaining ground water samples (S-2 to S-15) have their concentrations of Na+ below the threshold limit (200 mg/L) of WHO19.

 

Potassium (K+):

All the fifteen ground water samples (S-1 to S-15) have low concentrations of K+ ranging from 0.9 mg/L to 2.2 mg/L (table-3). S-1 has highest concentration of K+ (2.2 mg/L) while those of S-9, S-13 and S-15, are the lowest (0.9 mg/L).

 

Chloride (Cl-):

For the fifteen ground water samples (S-1 to S-15), the concentrations of Cl- range from 4.3 mg/L to 632.4 mg/L (table-3).Except S-1, other remaining ground water samples (S-2 to S-15) have their concentrations of Cl- below the acceptable limit (250 mg/L) while that of S-1,is below the permissible limit (1000 mg/L) of BIS standard for drinking water18.

 

Ground water quality for irrigation:

The values of RSC (residual sodium carbonate) and SAR (sodium adsorption ratio) for the fifteen ground water samples (S-1 to S-15), are detailed below in table-4:

 

 


 

Table-4: Values of RSC and SAR for ground water samples

Sample code no.

S-1

S-2

S-3

S-4

S-5

S-6

S-7

S-8

S-9

S-10

S-11

S-12

S-13

S-14

S-15

RSC values

(meq/L)

0.35

1.80

1.99

1.27

1.49

1.44

5.68

1.57

1.04

2.63

1.72

1.42

2.48

3.89

1.18

SAR values

9.5

1.3

1.6

1.1

1.3

1.1

5.8

1.3

0.9

2.7

1.5

1.1

1.5

2.9

0.7

 


From the above table, it is clearly seen that ground waters represented by S-1, S-9 and S-15 have their RSC values below 1.25 meq/L and belong to excellent category (RSC value < 1.25 meq/L) for irrigation purpose while S-2 to S-6, S-8 and S-11 to S-13 belong to good quality category (RSC value in the range 1.25-2.5
meq/L) 1,16.

               

Again, the electrical conductivity values for S-2 to S-15 are within the category of good quality for irrigation (250-750 µS/cm).17

 

Above all, the values of SAR for the fifteen ground water samples (S-1 to S-15) range from 0.7 to 9.5 and thus all of them belong to the excellent category of water for irrigation (SAR value upto 10) 1,17. Therefore, all the ground waters represented by S-1 to S-15, are fit for irrigation purpose.

 

Statistical analysis on the basis of correlation co-efficient (r) values:

The values of correlation co-efficient (r) of different variable pairs of physico-chemical parameters for the fifteen ground water samples (S-1 to S-15), are shown in table -5 given below:

 


 

 

Table-5: Correlation co-efficient( r) values between different variable pairs of physico-chemical parameters for different  ground water samples

 

Temp.

pH

TDS

EC

TA

HCO3-

TH

Ca2+

Mg2+

Na+

K+

Cl-

Temp.

1

 

 

 

 

 

 

 

 

 

 

 

pH

-0.026

1

 

 

 

 

 

 

 

 

 

 

TDS

0.328

-0.003

1

 

 

 

 

 

 

 

 

 

EC

0.314

-0.001

0.999

1

 

 

 

 

 

 

 

 

TA

0.508

0.260

-0.165

-0.184

1

 

 

 

 

 

 

 

HCO3-

0.508

0.260

-0.165

-0.184

1

1

 

 

 

 

 

 

TH

0.288

-0.683

0.247

0.248

-0.120

-0.120

1

 

 

 

 

 

Ca2+

0.102

-0.604

0.134

0.138

-0.246

-0.246

0.947

1

 

 

 

 

Mg2+

0.432

-0.693

0.328

0.325

0.004

0.004

0.956

0.811

1

 

 

 

Na+

0.316

0.108

0.979

0.977

-0.105

-0.105

0.063

-0.048

0.159

1

 

 

K+

0.046

0.072

0.753

0.751

-0.295

-0.295

-0.033

-0.087

0.021

0.783

1

 

Cl-

0.249

-0.032

0.993

0.995

-0.276

-0.276

0.269

0.175

0.329

0.962

0.760

1

               


From table-5 above, it is clearly seen that strong positive correlation (r=0.999) is there between TDS and electrical conductivity (EC). Both Ca2+ and Mg2+ show strong positive correlations with total hardness (TH) having r values 0.947 and 0.956 respectively, establishing the fact that high concentrations of Ca2+ and Mg2+ attribute to more hardness of different waters. Strong negative correlation (r=-0.683) between pH and total hardness, indicates that with increase of pH, the total hardness for different ground water samples decreases and vice-versa. Cl- shows strong positive correlations with both Na+ and K+ having r values 0.962 and 0.760 respectively showing that both Na+ and K+ exist as chlorides in the different ground waters represented by S-1 to S-15. Further, Na+, K+ and Cl- show strong positive correlations with TDS having r values equal 0.979, 0.753 and 0.993 respectively. Similarly, Na+, K+ and Cl- show strong positive correlations with EC (r=0.977, 0.751 and 0.995 respectively).

The above strong positive correlations of Na+, K+ and Cl- with TDS and EC respectively, establish the fact that high values of TDS (and hence EC) are due to presence of NaCl and KCl salts mainly in the different ground waters represented by S-1 to S-15.

 

CONCLUSIONS:

On the basis of the above discussions based  on various experimental data and various correlation co-efficient (r) values of different pairs of physico-chemical parameters for fifteen different ground waters (S-1 to S-15), the following conclusions are drawn:

 

(i)       Ground water represented by S-1 is unfit for drinking purpose as many of the parameters have their values far above the acceptable limits of BIS standard for drinking water and that of WHO respectively.

(ii)     Ground waters represented by S-2 to S-15 may be used for drinking and other domestic purposes in absence of alternate sources.

 

However, some suitable treatments are necessary so as to keep the high values of the following parameters below the corresponding acceptable limits of BIS standard for drinking water –

a)       treatment of high values of total alkalinity for S-2 to S-15

 

b)       treatment of high values of total hardness for S-2 to S-6, S-8 to S-9, S-12 and S-15

 

c)       treatment of high values of Mg2+ for S-1, S-4 and S-6.

 

(iii)    Ground waters represented by S-1 to S-15 are fit for irrigation purpose.

 

(iv)   Strong positive correlations of Cl- with Na+ and K+ respectively, show the presence of NaCl and KCl salts in the different ground waters and further these two salts are mainly responsible for high values of TDS (and consequently high values of EC) of the different ground water samples.

 

ACKNOWLEDGEMENTS:

The author is thankful to the principal, D.M. college of Science, Imphal for the laboratory facilities provided for this research work and also to those local people of different sampling sites, for the co-operation extended by them.

 

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Received on 04.12.2015         Modified on 10.12.2015

Accepted on 26.12.2015         © AJRC All right reserved

Asian J. Research Chem. 8(12): December 2015; Page 733-738

DOI: 10.5958/0974-4150.2015.00118.2