Monitoring
the Concentration of Lead in the Industrial Wastewater of Baloda Bazar District
Keshar
Verma1, Sudheer Bhoi1, Yash Parhad1, Manas
Kanti Deb2
1School of
Studies in Environmental Science, Pt. Ravishankar Shukla University, Raipur CG
2, School of Studies in Chemistry, Pt. Ravishankar Shukla
University, Raipur CG
*Corresponding Author: bhoisudheer08@gmail.com
Abstract
Cement
manufacturing Industries is one of the key sectors of the Indian Economy which
has been rapidly growing at a rate over 8% and it is estimated to grow more.
Balodabazar is known as the Cement Hub of Chhattisgarh, most of the cement
industries are running in Balodabazar district of Chhattisgarh. They use plenty
of water for the cooling processes at the time of cement manufacturing and
discharging effluents into streams and rivers by polluting nearby water resources.
In this work, the waste water quality assessment study is attempted by
examining the physic-chemical parameters viz. Temperature, pH, Electrical
Conductivity (EC), TDS, DO, Total hardness, Na+, K+, Ca2+,
Mg2+, CL-, SO42-, NO3-,
and PO43-and also analysis of heavy metal element
(lead) is described.
The abundance of cations and anions in the analyzed waste water sample
is Ca (%)>Mg (%)>Na (%)> K (%) and SO42-(%)>Cl-
(%)>NO3- (%)> PO43- (%) respectively.
The waste water is found to be acidic in nature and out of 17 samples 6-7
samples are contaminated by lead. It is inferred that the study area is
moderately suitable. Almost all water bodies in India have been found to be
contaminated by industrial activities. Although the CPCB’s strict guidelines
apply to all industries in India, the current state of the environment is far
from ideal.
Keywords: physic-chemical parameters, industrial effluents,
waste water, pollution, Baloda bazar district, India
Introduction
In
previous days, wood was the main material for the construction of buildings,
but now cement has taken its place. Due to indispensable nature of cement
industry, it plays a major role in improving the living standard of human
society. (3) Industrial waste water is one
of the major contaminating sources in pollution of the water environment.
Industries that use plenty of water for the processing have the potential to
pollute waterways by discharging their wastes into the waterways. An industrial
effluent of cement contains variety of chemicals and harmful products which
spoils the soil quality, plants and aquatic life through various sources. (2)
Wastewater
containing heavy metal constituents are mainly generated from industrial
processes, Heavy metals are very dangerous in nature and causing carcinogenic
because they can easily bio-accumulate in our bodies and resulting in increase
of concentration of chemicals in the biological organism. A special emphasize
in this study is on lead it is the most common toxic heavy metals in some
inorganic industrial wastewater. (6)
Lead
poisoning or exposure of high levels of lead may cause anemia, weakness, kidney
failure, brain damage and very high exposure of lead may also cause death. Lead
can cross the placental barrier, which means pregnant women who are exposed to
lead can also exposed their unborn child. Lead can damage a developing baby’s
nervous system. Cement is manufactured using clay, limestone in the ratio of
1:3 and mixed with 3% of gypsum and form the powdered substance (made into
slurry by adding water in the wet process) and feeding into rotatory kiln. A
flame of coal fire leaps up the tower at around 1400 0C, cement is formed. (2) The four main constituents of cement are
dicalcium silicate, tricalcium silicate, tricalcium aluminate and tetra calcium
aluminoferate(2) The effluent from cement
industries mainly contains processed water, dissolved solids (Potassium and
sodium hydroxide, chlorides and sulphates) and suspended solids (Calcium
carbonate) when these mixed with the receiving water, it may trigger a
synergetic changes in heavy metal contains pH, temperature, color,
conductivity, suspended solids. The studied data of various physiochemical
parameters are useful for providing the information about the nature of water
environment. This study will provide specific information about the water
quality standard of specific area. (5)
Materials
and methods
Location
and Geology of study area
The
geographical status of Balodabazar city is in the middle of 21.3000 54’ to
31.450 14’ Latitude and 42.020 17’ to 80.290 07’Longitude and in the height of
270meter from the mean sea level. Balodabazar is also called the Cement hub of Chhattisgarh because
there are many reputed cement plant is situated like Ultra Tech Cement Hirmi,
Grasim Cement Rawan, Ambuja Cement Ravan, Nuvoco Cement (Earlier Lafarge
Cement) sonadih, Nu Vista Cement (Earlier Emami cement ) Risda, Shree Cement
Khapradih. In this work, the quality of waste water released by the above
mentioned industries are described.
Water
Sampling Procedure
Sixteen wastewater samples from five industries were
taken .Sampling was carried out in the month of March (2022). Sampling involves
taking 3-4 samples at each Industrial site from the various sampling locations.
Before sampling 1 liter Polyethylene container was washed with detergent and
dried to ensure that all water in the container evaporated. The containers were
labeled accordingly with the alphabets or numbers.
After
sampling nitric acid was dropped into
all the polyethylene containers for sample preservation as described by Michael
(1982) and APHA (1992).
3.1.1
Sampling Points
S.No.
|
Samples
|
Location
|
Longitude/Latitude
|
1
|
Sample 1
|
Ultratech (Ameri)
|
21.560330/81.955688
|
2
|
Sample 2
|
Ultratech (Paraswani)
|
21.558516/81.956987
|
3
|
Sample 3
|
Ultratech (Kuthraud)
|
21.552432/81.957211
|
4
|
Sample 4
|
Ultratech (Saklor)
|
21.551384/81.961198
|
5
|
Sample 5
|
Ultratech (khapradih)
|
21.602791/82.035929
|
6
|
Sample 6
|
Ultratech (Ravan)
|
21.575962/82.014650
|
7
|
Sample 7
|
Shree Cement (Padkidih)
|
21.617857/82.022090
|
8
|
Sample 8
|
Shree Cement (Khapradih)
|
21.605128/82.038964
|
9
|
Sample 9
|
Shree Cement (Karhi)
|
21.626855/82.026408
|
10
|
Sample 10
|
Emami (Risda)
|
21.634188/82.108260
|
11
|
Sample 11
|
Emami (Khelwardih)
|
21.634459/82.089198
|
12
|
Sample 12
|
Ambuja (Rawan)
|
21.675473/82.100648
|
13
|
Sample 13
|
Ambuja (Pausari)
|
21.684381/82.109754
|
14
|
Sample 14
|
Ambuja (Maldi)
|
21.669546/82.053950
|
15
|
Sample 15
|
Lafarge (Raseda)
|
21.727288/82.209194
|
16
|
Sample 16
|
Lafarge (Sonadih)
|
21.754183/82.195402
|
3.2
Water Quality Parameters
3.2.1
Physico-chemical Characteristics
Inorganic compounds and Organic compounds are the main
in-charge for the pollution of water. They determine the measure of hardness,
dissolved oxygen, biological oxygen demand, chemical oxygen demand, alkalinity
etc. It is also caused by various microbial activities of microorganisms. The
parameters such as pH, EC, TDS, hardness, COD and heavy metals know about the
status of pollution in industrial wastewater were analyzed.
Color is a qualitative feature of water. With the help
of its general condition, the water pollution can be assumed. If the color is
dark grey or black, the water is typically septic, having undergone extensive
bacterial decomposition under anaerobic conditions. The color of the sample was
compared with the glass comparator and colorless distilled water. Color of
water is determined using (HANNA POCKET SPECTROPHOTOMETER – HI727)
pH is considered to be the most important water
parameter. The pH of Wastewater were less than 6 that means corrosive in nature
and those having pH more than 9 will cause some metal ions to precipitate as
carbonates or hydroxides. In this study, the extracted water sample were used
for the analysis of pH by using (HANNA ANALYSER HI991300, 8424, 9142 pH/EC
METER. )
Electrical conductivity shows the significant
correlation with various other parameters. The electrical conductivity was
measured with the help of an electrical conductivity meter (HANNA ANALYSER
HI991300, 8424, 9142 pH/EC METER. ) Which determine the resistance offered by
the water between two Platonized electrodes.
The suspended and dissolved solids in river water are
considered as total solids. Solids that are able to settle can be removed by
sedimentation. The extracted water samples were used for the analysis of TDS by
using HANNA ANALYSER HI991300, 8424, 9142 pH/EC METER.Turbidity is an optical
property which broadly describes the clarity or cloudiness of water. It is
related to color, but with has more to do with the loss of transparency due to
the effect of suspended particles and colloidal material. Turbidity of sample
water is measured using (DIGITAL TURBIDITY METER, Model no.-331)
Dissolved oxygen (DO) is the relative measure of the
amount of oxygen (O2) dissolved in water. DO and O2 is
measured using (HANNA PORTABLE DISSOLVED OXYGEN METER - HI9146) Hardness is produced in water due to
various reasons by multivalent metallic cations. The total hardness in water is
defined as the summary absorption of calcium and magnesium cations expressed in
milligram equivalents per kilogram or microgram equivalents per kilogram.
Hardness is determined by the EDTA method by alkaline condition. When EDTA was
added as a titrate, Ca and Mg divalent ions formed complexes resulting in a
sharp change from wine red to blue which indicates endpoint of the titration
(Kaur and Malik, 2012; Islam et al., 2015).The concentration of sodium,
potassium and lithium were determined by flame photometer (ANALAB FLAME PHOTOMETER) Calcium
and Magnesium ion concentration was calculated using by EDTA titration method
and P&R, EBT indicator.
Sulfate (SO42-) ion was
determined by using the ion selective method, by the taking ultra clean
distilled water as a reference.Nitrate (NO3-)
concentration in industrial waste water was measured, by multiplying value of
Ammonia with factor “3.63”. Ammonia is
determined using pocket spectrophotometer (HI 733 Ammonia HR).Phosphate (PO43-)
concentration in industrial waste water was measured, by multiplying value of
Phosphorus with factor “3”. The value of Phosphorus is determined using pocket
spectrophotometer (HI 736 Phosphorus ULR). By using dilution factor of 1:3.
Major
Identification of Lead
Central
India is rich in deposits of natural resource materials such as coal, pyrite,
dolomite and alumina that contain Pb, and other heavy metals at the trace
levels, and the substantial exploitation of these materials has tended to
increased contamination of water and geological formations.
Result
and Discussion
Table 1: Physical Parameter
of Industrial wastewater of Balodabazar District
S.N.
|
Samples
|
pH
|
Temp
(°C )
|
TDS
(mg/L)
|
EC
(µs/cm)
|
Salt
(mg/L)
|
DO
(mg/L)
|
O2 (%)
|
COLOR
|
TURBIDITY
|
1
|
S-1
|
5.8
|
30.2
|
840.6
|
793
|
657
|
4.46
|
62.7
|
35
|
11
|
2
|
S-2
|
6.2
|
28.9
|
1363
|
1363
|
9260
|
5.64
|
74.5
|
75
|
41
|
3
|
S-3
|
6.7
|
28.6
|
1772
|
772
|
1040
|
5.64
|
67.2
|
20
|
3
|
4
|
S-4
|
6.3
|
29
|
717.1
|
1717
|
1007
|
5.56
|
79.1
|
25
|
7
|
5
|
S-5
|
6.1
|
29.1
|
1966
|
1966
|
1191
|
5.69
|
63.4
|
20
|
0
|
6
|
S-6
|
5.9
|
29.9
|
963
|
1994
|
900
|
5.02
|
80.6
|
59
|
63
|
7
|
S-7
|
5.6
|
29.5
|
1646
|
1540
|
9580
|
5.04
|
70.4
|
116
|
73
|
8
|
S-8
|
6.8
|
28.1
|
176.3
|
646
|
1041
|
5.6
|
73.4
|
15
|
4
|
9
|
S-9
|
6.3
|
29
|
1603
|
1766
|
9200
|
5.09
|
69.3
|
5
|
3
|
10
|
S-10
|
6.9
|
29.4
|
767
|
1603
|
1043
|
5.34
|
79.3
|
5
|
2
|
11
|
S-11
|
5.9
|
30.4
|
1902
|
1764
|
1026
|
6.05
|
81.3
|
10
|
2
|
12
|
S-12
|
5.4
|
30.6
|
906
|
1926
|
1147
|
6.49
|
80.7
|
25
|
13
|
13
|
S-13
|
6.5
|
28.4
|
1147
|
720
|
985
|
5.97
|
76.4
|
106
|
51
|
14
|
S-14
|
6.8
|
28.5
|
1708
|
1640
|
456
|
5.84
|
85.9
|
40
|
24
|
15
|
S-15
|
6.4
|
28.7
|
968.6
|
846
|
9203
|
6.34
|
74.3
|
95
|
63
|
16
|
S-16
|
6.7
|
29
|
1983
|
1602
|
1041
|
6.03
|
86.7
|
65
|
72
|
Temperature
Temperature
can be controls behavioral characteristics of organism’s solubility of gases
and salts in water. Disease resistance is also linked to temperature. The
temperature of industrial waste water was given in (Table 1). A slight variation in
temperature of the waste water was observed during the measured, ranging from 28.1-30.6°C with the mean value of 29.20
Acidity
(pH)
The
Acidity of water is measured in the term of pH value. The toxicity of heavy
metals also gets enhanced at particular pH. Thus, pH is having primary
importance to deciding the quality of waste water effluent. The pH value of
industrial effluent samples was given (Table 1). The range of desirable pH of water
prescribed for drinking purpose is 6.5-
8.5 (ISI and WHO). The range of pH value of effluent samples collected from
different industrial is 5.4-6.9 with the mean value of 6.26
in the industrial effluent samples. The industrial waste water was found
acidic in nature.
Electrical
conductivity (EC)
Electrical conductivity was found with the
range of 646-1966µs/cm with the mean value of 1416.13µs/cm. The
electrical conductivity of industrial effluent samples was given in (Table1).Conductivity
is a good indicator to assess waste water quality. In present study high EC
level was found with high saline. The EC value was good correlated with Na+,
Mg+, TDS, Hardness and Alkalinity.
Total
dissolved solid (TDS)
TDS value of the industrial waste water was
summarized in (Table 1). TDS values were found the range of 176.3-1966mg/L with the mean
value of 1276.79mg/L. The TDS value was good correlation with EC.
Hardness
The total hardness of the industrial waste water was
summarized in (Table 1). The
concentration varied from 160-940 mg/L with the mean value of 431.006mg/L.
The total hardness was good correlated with EC, Na+, and NH4+.
Dissolved
oxygen (DO)
Dissolved oxygen of the industrial waste water
was found ranged from 4.46-6.49 mg/L with the mean value of 5.6125
mg/L. Its correlation with water body
gives direct and indirect information e.g. bacterial activity, photosynthesis,
availability of nutrients, stratification etc. dissolved oxygen decreased due
to increase in temperature and also due to increased microbial activity. The dissolved oxygen was
summarized in(Table 1).
Figure: 1. Correlation between pH and Cl-
Figure: 2. Correlation between pH and NO3-
Figure: 3. Correlation between pH and PO43-
Figure: 4. Correlation between Conductivity
and (Cl-)
Figure: 5. Correlation between Conductivity
and Na+
Figure: 6. Correlation between Conductivity
and Mg2+
Figure: 7. Correlation between Conductivity
and Turbidity
Figure: 8. Correlation between Conductivity
and Hardness
Figure: 9. Correlation between Conductivity
and TDS
Figure: 10. Correlation between Conductivity
and pH
Table 2: Chemical Parameter of Industrial
wastewater of Balodabazar District
S.N.
|
Samples
|
Na+
(mg/L)
|
K+
(mg/L)
|
Ca+
(mg/L)
|
Mg+
(mg/L)
|
TH
(mg/L)
|
Cl-
(mg/L)
|
SO42-
(mg/L)
|
NO3-
(mg/L)
|
PO43- (mg/L)
|
1
|
S-1
|
92
|
98
|
740
|
140
|
880
|
72.5
|
243
|
14.2
|
1.368
|
2
|
S-2
|
62
|
72
|
212
|
48
|
260
|
38.2
|
806
|
13
|
1.116
|
3
|
S-3
|
15
|
18
|
156
|
44
|
205
|
29.7
|
1372
|
12.7
|
1.251
|
4
|
S-4
|
18
|
6
|
232
|
68
|
300
|
128
|
1320
|
11.7
|
1.15
|
5
|
S-5
|
17
|
52
|
352
|
48
|
400
|
56.8
|
1832
|
39.6
|
1.197
|
6
|
S-6
|
63
|
47
|
874.6
|
66.2
|
940.8
|
82.4
|
2206
|
42.2
|
1.404
|
7
|
S-7
|
63
|
51
|
689.2
|
71.6
|
760.8
|
81.7
|
503
|
41.6
|
1.278
|
8
|
S-8
|
17
|
17
|
189
|
50.6
|
239.6
|
53.3
|
906
|
9.8
|
1.107
|
9
|
S-9
|
16
|
17
|
269
|
51
|
320
|
42.6
|
353
|
8.02
|
1.332
|
10
|
S-10
|
21
|
3
|
128
|
36.8
|
164.8
|
95.9
|
278
|
9.63
|
1.125
|
11
|
S-11
|
20
|
7
|
204
|
56
|
260
|
20.9
|
1585
|
8.96
|
1.87
|
12
|
S-12
|
66
|
59
|
196
|
16
|
212
|
43.2
|
1896
|
38.9
|
1.179
|
13
|
S-13
|
37
|
45
|
126
|
34
|
160
|
135
|
496
|
36.5
|
0.8
|
14
|
S-14
|
22
|
22
|
102
|
22
|
124
|
88.8
|
726
|
10.9
|
1.17
|
15
|
S-15
|
31
|
15
|
840
|
101
|
940.6
|
129
|
487
|
13.3
|
1.179
|
16
|
S-16
|
38
|
18
|
650
|
78.5
|
728.5
|
42.8
|
1509
|
36.7
|
1.323
|
Sodium and Chloride
The
Na+ and Cl- concentration in
industrial waste water of this region is summarized in (Table- 2). The concentration of
Na+ and Cl- was ranged from 15-92 mg/L and 20.85-135.35 mg/L with the mean value of 37.37 mg/L and 71.26 mg/L,
respectively. High Na+ and
Cl- value were observed
in the waste water of many industries of this region. The Na+ concentration was good correlation with the value of
EC, Cl-, SO42-,
NO3-, and PO43-.
The Cl- concentration
was good correlated with the value ofEC,
Na+,K+, Ca2+and Mg2+.
Calcium and Magnesium
The
Ca2+ and Mg2+ concentration in
industrial waste water of this region is summarized in (Table- 2). The concentration of
Ca2+ and Mg2+ was ranged from 102-874mg/L and 16-140 mg/L with the mean value of 372.48 and 58.20 mg/L,
respectively. The calcium concentration was good correlation with the value of Cl-and SO42-. The Mg2+ concentration was good correlated with the value of
Cl- and SO42-.
Potassium (K+)
The
K+ concentration in
industrial waste water of this region is summarized in (Table- 2). The K+ concentration in
industrial waste water of this region is very high and ranged from 3-98 mg/L with the mean value of 34.14 mg/L.K+ ion has a good
correlation with value of EC, Cl-,
SO42-, NO3-and PO43-.
Nitrate
The
NO3-
concentration in industrial waste water of this region is high and summarized
in (Table-
2). The NO3-
concentration in industrial waste water was found ranged from 8.02-42.17 mg/L with the mean value of 21.71 mg/L. NO3-ions
has a good correlation with value of Na+and
K+.
Sulfate (SO42-)
The
SO42- content
in industrial waste water was summarized in (Table-2). The SO42- content in
industrial waste water of this region is ranged from 243-2206 mg/L with the mean value of 1032.37mg/L.The sulfate concentration was good correlated with EC, Na+, K+, Ca2+,
and Mg2+.
Phosphate (PO43-)
The
PO43-
concentration in industrial waste water of this region is summarized in (Table- 2).
The PO43-
concentration in industrial waste water of this region is ranged from 0.8-1.4 mg/L with the mean value of 1.240
mg/L. PO43-ion
has a good correlation with value of Na+
and K+.
Figure: 11. Correlation between Conductivity
and SO42-
Figure: 12. Correlation between Conductivity
and PO43-
Figure: 13. Correlation between (Mg2+)
and Hardness
Figure: 14. Correlation between (Ca2+)
and Hardness
Figure: 15. Correlation between (Na+)
and Cl-
Figure: 16. Correlation between (Ca2+)
and Mg2+
Figure: 17. Correlation between (Ca2+)
and Hardness
Figure: 18. Correlation between (Mg2+)
and Hardness
Figure: 19. Correlation between (K+) and
Turbidity
Figure: 20. Correlation between pH and (K+)
Spatial Distribution
Figure: 21. Spatial Distribution of Cations
Spatial Distribution
Figure: 22. Spatial Distribution of Anions
Figure: 23. Relative abundance of ions in the
Industrial waste water.
Correlation Coefficient Analysis
The correlation matrix of water quality
parameters examined was presented in Table24, which indicates –
●
-1 indicates a perfectly negative linear correlation between two
variables.
●
0 indicates no linear correlation between two variables.
●
1 indicates a perfectly positive linear correlation between two
variables.