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.
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