Physico-chemical
assessment of ground water qualities of some areas of Imphal East district of
Manipur during post-monsoon – 4th
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 (represented by S-1 to S-15) were collected from different
locations of Imphal East district of Manipur during post-monsoon of 2014. They
were analyzed for physico-chemical parameters like 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-. Only ground waters represented by S-14 (of Achanbigei Makha
Leikai) and S-15 (of Achanbigei Mayai Leikai) are found to be fit for drinking
purpose from physico-chemical analysis point of view. However, ground waters
represented by S-1 to S-13 may also be used for drinking purpose in absence of
alternate sources and further it is necessary to treat them so as to keep high
values of total alkalinity (for S-1 to S-13) and total hardness value for S-3
within acceptable limit (200 mg/L) of BIS standard for drinking water. All the
fifteen ground waters are fit for other domestic purposes also. Besides these,
all the fifteen ground waters (S-1 to S-15) are fit for irrigation purpose also.
Further,
strong positive correlations exist between TDS and each of electrical
conductivity and total alkalinity for the ground waters (S-1 to S-15). Again
correlation co-efficient data reveals that presence of NaHCO3 and
KHCO3 in such ground waters, attribute to high values of both TDS
(and hence EC) and total alkalinity (TA). Further, strong correlations of Ca2+
and Mg2+ with TH (total hardness), indicate the direct
proportionality of total hardness values to concentrations of Ca2+
and Mg2+ ions for the different ground waters (S-1 to S-15).
KEYWORDS: Physico-chemical parameters,
drinking, irrigation, , post-monsoon,
BIS and correlation co-efficient.
Of
the total global water resources, ground water is about 0.6% and out of this,
only 0.3% is extractable economically1. There is increasing demand
for ground water all over the world day by day to meet the requirements for
human consumption for drinking and other
domestic purposes, and also for irrigation as well as industrial purposes. This
increasing demand for ground water is because of the fact that with increasing
population growth all over the world, rate of urbanization increases and
consequently many places of surface water bodies in cities, towns and even in
villages are converted into sites for construction of houses, buildings,
offices, institutions, commercial areas, industrial sites etc. which leads to
decrease in surface water bodies to a large extent. And consequently, it leads
to more demand for ground water all over the world. But ground water is not always
safe for drinking, other domestic, irrigation and industrial purposes. It is,
therefore, necessary to monitor qualities of such ground water from time to
time. With a view to this objective, many researchers of different countries
had already started extensive investigations on qualities of ground water in
order to examine whether such ground waters are fit for drinking, other
domestic, irrigation and industrial purposes.2-7. In India also many
researchers of different states, studied on ground water qualities for
drinking, other domestic and irrigation purposes mainly.8-14
This
research work aims at carrying out physico-chemical assessment of ground water
qualities of some areas of Imphal East district of Manipur during post-monsoon
of 2014.
MATERIALS AND
METHODS:
Chemicals
used for this research work, were of AR grade and were used as received.
Fifteen ground water samples were collected from hand pumps of fifteen
different locations of Imphal East district of Manipur during post-monsoon of
2014. The geographical positions (longitudes and latitudes) for the different
sampling sites, were measured with a GPS instrument and they are detailed in
table –1 below:
Table-1: Locations of different sampling sites (with
geographical positions)
|
Sample code no. (with source) |
Sampling sites (locations) |
Longitude |
Latitude |
|
S-1 (Hand pump) |
Kairang Awang Leikai (1) (Near Primary School) |
93057/15.48//E |
24050/45.27//N |
|
S-2 (Hand pump) |
Kairang Awang Leikai (2) |
93057/19.79//E |
24050/49.62//N |
|
S-3 (Hand pump) |
Kairang Chingya (1) (Near foothill) |
93057/43.66//E |
24050/59.45//N |
|
S-4 (Hand pump) |
Kairang Chingya (2) (Near paddy field) |
93057/45.99//E |
24050/58.26//N |
|
S-5 (Hand pump) |
Heingang Mayai Leikai |
93056/45.46//E |
24051/38.21//N |
|
S-6 (Hand pump) |
Heingang Awang Leikai (Near foothill) |
93056/25.19//E |
24052/19.78//N |
|
S-7 (Hand pump) |
Khundrakpam Awang Leikai (near foot hill) |
93059/24.54//E |
24053/34.09//N |
|
S-8 (Hand pump) |
Tangkham Maning Leikai (Near big pond) |
93058/30.19//E |
24053/59.52//N |
|
S-9 (Hand pump) |
Chingkhu Awang Leikai (Near foothill) |
93059/21.91//E |
24054/25.66//N |
|
S-10 (Hand pump) |
Wangkhei Khunou (Near foothill) |
93059/51.32//E |
24055/47.78//N |
|
S-11 (Hand pump) |
Sinam kairangthel (Near foothill) |
93058/59.35//E |
24056/50.62//N |
|
S-12 (Hand pump) |
Yumnam Khunou Awang Leikai Sanjenbam (Near foothill) |
94000/12.94//E |
24056/24.35//N |
|
S-13 (Hand pump) |
Ishikha (Ichikha) Awang Leikai (Near foothill) |
94000/31.34//E |
24056/19.05//N |
|
S-14 (Hand pump) |
Achanbigei Makha Leikai |
93056/05.39//E |
24052/06.80//N |
|
S-15 (Hand pump) |
Achanbigei Mayai Leikai |
93056/08.55//E |
24052/21.20//N |
All
the ground water samples were collected in well sterilized polythene bottles of
onr litre capacity each. For sampling and preservation, strict guidelines were
followed15. The fifteen ground water samples were analyzed for physico-chemical parameters such as
temperature, pH, TDS ( total dissolved solids) and electrical conductivity
(EC), total alkalinity(TA), CO32-, HCO3-
total hardness (TH), Ca2+ , Mg2+, Na+, K+
and Cl-. Parameters such as temperature, pH, TDS and
electrical conductivity were measured during sampling for each ground water
sample while parameters such as total alkalinity, total harness, Ca2+
and Cl- were determined in
departmental research laboratory using standard methods15.
Concentration values of parameters like CO32-, and HCO3-
were calculated from corresponding total alkalinity values while that of Mg2+,
were calculated from the difference of total hardness and calcium hardness for
each ground water sample. Furhter concentrations of Na+ and K+
for each ground water sample, were determined using a flame photometer
instrument. Brief methods and instruments /equipments used for determinations
and measurements of various physico-chemical paramenters are shown in table-2
given below:
|
Table-2 : Instruments and brief methods used
for measurements and determinations of physico-chemical parameters of ground
water samples |
|
|
Physico-chemical parameters measured /
determined |
Instruments and brief
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) |
The
values of parameters such as RSC (residual sodium carbonate) and SAR (sodium
adsorption ratio) which were used for assessing irrigation water quality for
the different ground water samples, were calculated using the following
relationships16-17:
where
ionic concentrations were expressed in
milli-equivalents / litre (meq/L).
RESULTS AND
DISCUSSION:
All
the fifteen ground water samples (S-1 to S-15) were found to be colourless and
odourless. The values of different physico-chemical parameters for the
different ground water samples, are detailed in table-3 given below:
|
Table-3:
Values of physico-chemical parameters for ground water samples |
||||||||||||
|
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 |
23.3 |
6.7 |
309 |
660 |
350 |
427 |
140 |
21.6 |
20.9 |
91.2 |
1.2 |
7.1 |
|
S-2 |
23 |
7 |
356 |
746 |
395 |
481.9 |
144 |
21.6 |
21.9 |
105.7 |
1.3 |
11.3 |
|
S-3 |
22.8 |
7.3 |
277 |
603 |
290 |
353.8 |
222 |
42.5 |
28.2 |
48.1 |
1 |
31.2 |
|
S-4 |
22.4 |
7.4 |
342 |
732 |
320 |
390.4 |
182 |
29.7 |
26.2 |
90.3 |
1.3 |
62.4 |
|
S-5 |
22.3 |
7 |
243 |
533 |
270 |
329.4 |
96 |
17.6 |
12.6 |
66.5 |
1.5 |
9.9 |
|
S-6 |
22.2 |
7.4 |
228 |
487 |
270 |
329.4 |
164 |
32.1 |
20.4 |
49.4 |
1.1 |
5.7 |
|
S-7 |
23.2 |
7.4 |
208 |
454 |
250 |
305 |
164 |
32.1 |
20.4 |
38.5 |
0.9 |
7.1 |
|
S-8 |
22.3 |
7.7 |
402 |
854 |
490 |
597.8 |
148 |
27.3 |
19.4 |
148.9 |
1.2 |
12.7 |
|
S-9 |
23.8 |
7.5 |
275 |
586 |
325 |
396.5 |
116 |
20.8 |
15.6 |
94.6 |
1.1 |
7.1 |
|
S-10 |
23.3 |
7.3 |
193 |
413 |
220 |
268.4 |
156 |
24 |
23.3 |
31.9 |
0.8 |
5.7 |
|
S-11 |
21.8 |
7.5 |
226 |
493 |
270 |
329.4 |
118 |
23.2 |
14.6 |
67.3 |
0.9 |
4.3 |
|
S-12 |
22.2 |
7.4 |
223 |
487 |
265 |
323.3 |
194 |
32.1 |
27.7 |
34 |
1 |
5.7 |
|
S-13 |
22.4 |
7.2 |
210 |
456 |
250 |
305 |
186 |
32.1 |
25.8 |
28.7 |
0.8 |
5.7 |
|
S-14 |
19.9 |
7 |
160 |
343 |
175 |
213.5 |
62 |
12.8 |
7.3 |
39.1 |
1 |
5.7 |
|
S-15 |
21.6 |
6.8 |
161 |
343 |
175 |
213.5 |
66 |
12.8 |
8.3 |
37.5 |
1 |
5.7 |
On
the basis of values of different physico-chemical parameters for different
ground water samples (S-1 to S-15), the following discussion has been made:
Temperature:
Temperatures
for fifteen ground waters (S-1 to S-15) are in the range 19.9-23.80C
(table-3).S-14 has the lowest temperature (19.90C) while that
of S-9 is the highest (23.80C).
pH Values:
The
pH values for the fifteen ground water samples (S-1 to S-15) range from 6.7 to
7.7 (table-3). All these values are within the acceptable limit(6.5 - 8.5) of
BIS standard for drinking water as well as that of WHO18.-19 S-1 has lowest value of pH(6.7) while S-8 has
highest value of it (7.7).
TDS (Total dissolved solids):
The
TDS values for the fifteen ground water samples (S-1 to S-15) are in the range
160-402 mg/L (table-3). All these TDS values are below the acceptable limit
(500 mg/L) of BIS standard for drinking water18. S-14 has lowest
value of TDS (160 mg/L) while that of S-8 is highest (402 mg/L). As the TDS
values for the fifteen ground water samples are less than 1000 mg/L, all of
them may also be used for other domestic purposes not only for drinking purpose20.
Electrical conductivity (EC):
The
electrical conductivity values for the fifteen ground water samples (S-1 to
S-15) range from 343µS/cm to 854 µS/cm (table-3). Each of S-14 and S-15 has the
least value (343µS/cm) while that of S-8 is highest one (854 µS/cm).
Total alkalinity (TA):
The
values of total alkalinity for the fifteen ground water samples (S-1 to S-15)
are in the range 175 – 490 mg/L
(table-3). Each of S-14 and S-15 has least value of total alkalinity (175 mg/L)
while that of S-8 is highest (490 mg/L). Only S-14 and S-15 have total
alkalinity values below the acceptable limit (200 mg/L) of BIS standard for
drinking water while those of remaining ground water samples (S-1 to S-13) have
their values above the acceptable limit but below the permissible limit (600
mg/L)18.
CO32- and HCO-3:
The
concentrations of CO32- for all the ground water samples
(S-1 to S-15) are almost found to be zero
as the phenolphthalein alkalinity (P-alkalinity) for each of them is
zero. However, the concentrations of HCO3- for the ground
water samples range from 213.5 mg/L to 597.8 mg/L (table-3). Each of S-14 and
S-15 has least concentration of HCO3- (213.5 mg/L) while that of S-8 is
highest (597.8 mg/L).
Total hardness (TH):
The
total hardness values for the fifteen ground water samples (S-1 to S-15) are in
the range 62-222mg/L (table -3). S-3
has highest value of total hardness (222 mg/L) while S-14 has lowest value of
it (62 mg/L). S-1 to S-2 and S-4 to S-15 have their total hardness values below
the acceptable limit (200 mg/L) while that of S-3 is above the acceptable limit
but below the permissible limit (600 mg/L) of BIS standard for drinking water.18
Further,
S-14 and S-15 belong to soft water category (0-75 mg/L); S-1, S-2, S-5, S-8,
S-9 and S-11 belong to moderately hard water category (75-150 mg/L) while S-3,
S-4, S-6, S-7, S-10, S-12 and S-13 belong to hard water category (150-300
mg/L).20
Calcium (Ca2+):
The
concentrations of Ca2+ for the fifteen ground water samples (S-1 to
S-15) range from 12.8 mg/L -42.5 mg/L
(table-3). All the concentration values of Ca2+ for different ground
water samples, are below the acceptable limit (75 mg/L) of BIS standard for
drinking water.18 Both S-14 and S-15 have the lowest concentration
of Ca2+ (12.8 mg/L) while that of S-3 is highest (42.5 mg/L).
Magnesium (Mg2+):
The
concentrations of Mg2+ for
the fifteen ground water samples (S-1 to S-15) are in the range
7.3 – 28.2 mg/L (table-3). S-14 has lowest concentration of Mg2+
(7.3mg/L) while that of S-3 is highest (28.2 mg/L). However, all the
concentration values of Mg2+ for the fifteen ground waters (S-1 to
S-15), are below the acceptable limit (30 mg/L) of BIS standard for drinking
water.18
Sodium (Na+):
About
sodium contents for the fifteen ground water samples (S-1 to S-15), the
concentrations of sodium for different ground waters are in the range 31.9–148.9
mg/L (table-3). S-13 has lowest concentration of sodium (28.7 mg/L) while that
of S-8 is highest (148.9 mg/L). However, all the concentration values for the
fifteen ground waters, are below the threshold limit (200 mg/L ) of WHO.19
Potassium (K+):
All
the fifteen ground water samples (S-1 to S-15) have low concentrations of K+
ranging from 0.8 mg/L to 1.5 mg/L (table-3). Each of S-10 and S-13 has the
lowest concentration of K+ (0.8 mg/L) while that of S-5 is highest
(1.5 mg/L).
Chloride (Cl-):
The
concentrations of chloride for the fifteen ground water samples (S-1 to S-15),
are in the range4.3-62.4mg/L (table-3). S-11 has lowest concentration of Cl- (4.3 mg/L)
while that of S-4 is highest (62.4mg/L). However, all these concentration
values of Cl- for the fifteen ground waters(S-1 to S-15),are below
the acceptable limit (250 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 shown below in table-4:
|
Table-4: Values of RSC and SAR
for different 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) |
4.20 |
5.02 |
1.36 |
2.76 |
3.48 |
2.12 |
1.72 |
6.84 |
4.18 |
1.29 |
3.04 |
1.42 |
1.28 |
2.26 |
2.18 |
|
SAR values |
3.4 |
3.8 |
1.4 |
2.9 |
3.0 |
1.7 |
1.3 |
5.3 |
3.8 |
1.1 |
2.7 |
1.1 |
0.9 |
2.2 |
2.0 |
From
the above table-4, it is clearly seen that the values of RSC for different
ground water samples (S-1 to S-15),are in the range 1.28-6.84 meq/L. S-13 has
lowest value of RSC (1.28meq/L) while that of S-8 is the highest (6.84meq/L).
The values of RSC for S-3,S-6,S-7,S-10 and S-12 to S-15, are within the
category of good quality of water for irrigation(1.25-2.50 meq/L).1,16
From
table-3, it is seen that electrical conductivity values for S-1 to S-7 and S-9
to S-15 are within the category of good quality for irrigation (250-750 µS/cm).17
Above
all, the SAR values for S-1 to S-15, range from 0.9 to 5.3 and all these values
are below the excellent category of water for irrigation (SAR value upto 10) 1,17.
So, all the ground waters (S-1 to S-15) are fit for irrigation purpose.
Statistical analysis based on
correlation co-efficient (r) values:
The
calculated 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 detailed in table-5 given below:
Table-5: Correlation Co-efficient( r)
values between variable pairs of various physico-chemical parameters for
different ground water samples
|
|
Temp. |
pH |
TDS |
EC |
TA |
HCO3- |
TH |
Ca2+ |
Mg2+ |
Na+ |
K+ |
Cl- |
|
Temp. |
1 |
|
|
|
|
|
|
|
|
|
|
|
|
pH |
0.177 |
1 |
|
|
|
|
|
|
|
|
|
|
|
TDS |
0.410 |
0.267 |
1 |
|
|
|
|
|
|
|
|
|
|
EC |
0.413 |
0.279 |
0.999 |
1 |
|
|
|
|
|
|
|
|
|
TA |
0.429 |
0.341 |
0.959 |
0.958 |
1 |
|
|
|
|
|
|
|
|
HCO3- |
0.429 |
0.341 |
0.959 |
0.958 |
1 |
1 |
|
|
|
|
|
|
|
TH |
0.374 |
0.440 |
0.339 |
0.357 |
0.299 |
0.299 |
1 |
|
|
|
|
|
|
Ca2+ |
0.537 |
0.531 |
0.240 |
0.263 |
0.224 |
0.224 |
0.951 |
1 |
|
|
|
|
|
Mg2+ |
0.261 |
0.345 |
0.390 |
0.404 |
0.335 |
0.335 |
0.973 |
0.854 |
1 |
|
|
|
|
Na+ |
0.061 |
0.231 |
0.905 |
0.898 |
0.917 |
0.917 |
-0.051 |
-0.111 |
-0.003 |
1 |
|
|
|
K+ |
0.067 |
-0.209 |
0.603 |
0.604 |
0.507 |
0.507 |
-0.185 |
-0.245 |
-0.130 |
0.627 |
1 |
|
|
Cl- |
0.071 |
0.181 |
0.469 |
0.479 |
0.226 |
0.226 |
0.408 |
0.361 |
0.416 |
0.253 |
0.357 |
1 |
From
the above table-5, it is clearly seen that TDS shows very strong positive
correlations with both EC and TA (r=0.999 and 0.959 respectively) showing that
both EC and TA are directly proportional to TDS for different ground water
samples. Na+ shows very strong positive correlations with TDS, EC
and
CONCLUSIONS:
From
the above discussion based on various experimental results for fifteen
different ground water samples (S-1 to S-15), the following conclusions are
drawn:
(i) Only ground waters represented by S-14 and S-15, are fit
for drinking purpose as their corresponding values of physico-chemical
parameters, are below/ within the acceptable limits of BIS standard for
drinking water as well as that of WHO, as is evident from physico-chemical
analyses point of view.
(ii) In case of remaining ground waters (S-1 to S-13), they
are fit for drinking purpose in absence of alternate sources as their TA (total
alkalinity) values and total hardness value for S-3 are above the acceptable
limit but below the permissible limit of BIS standard for drinking water. So,
suitable treatment is necessary so as to keep the values of total alkalinity
for them within the acceptable limit of BIS standard for drinking water.
(iii) All the ground waters are suitable for other domestic
purposes.
(iv) All the ground waters (S-1 to S-15) are fit for
irrigation purpose.
(v) Strong positive correlations are shown between TDS and
each of electrical conductivity (EC) and total alkalinity (TA). From
correlation co-efficient values point of view, high values of both TDS (total dissolved
solids) and total alkalinity (TA) are due to presence of NaHCO3 and
KHCO3 mainly in different ground waters (S-1 to S-15). Further,
strong positive correlations of Ca2+ and Mg2+ with total
hardness (TH) reveals the dependence of high values of total hardness on high
concentrations of both Ca2+ and Mg2+ ions.
ACKNOWLEDGEMENTS:
The
author is mainly thankful to those local people of different sampling sites for
their cooperation extended to the author.
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Received
on 10.12.2015 Modified on 24.12.2015
Accepted
on 29.12.2015 © AJRC All right
reserved
Asian J. Research Chem. 8(12): December 2015; Page 751-756
DOI: 10.5958/0974-4150.2015.00121.2