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Author(s): Keshar Verma, Sudheer Bhoi, Yash Parhad, Manas Kanti Deb

Email(s): bhoisudheer08@gmail.com

Address: School of Studies in Environmental Science, Pt. Ravishankar Shukla University, Raipur CG.
School of Studies in Chemistry, Pt. Ravishankar Shukla University, Raipur CG.

*Corresponding Author: bhoisudheer08@gmail.com

Published In:   Volume - 36,      Issue - 1,     Year - 2023


Cite this article:
Verma, Bhoi, Parhad and Deb (2023). Monitoring the Concentration of Lead in the Industrial Wastewater of Baloda Bazar District. Journal of Ravishankar University (Part-B: Science), 36(1), pp. 38-57.



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.

 

 

Ph

Temp

TDS

EC

Salt 

DO

O2

COLOR

TURBIDITY

Na+

K+

Ca+

Mg+

TH

Cl-

SO42-

NO3-

PO43-

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

pH

1

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Temp

-0.79

1

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

TDS

-0.05

0.04

1

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

EC

-0.37

0.5

0.357

1

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Salt 

-0.2

-0.1

0.134

-0.04

1

 

 

 

 

 

 

 

 

 

 

 

 

 

DO

0.137

-0.1

0.147

0.04

-0.08

1

 

 

 

 

 

 

 

 

 

 

 

 

O2

0.22

0.05

0.004

0.36

-0.27

0.502

1

 

 

 

 

 

 

 

 

 

 

 

COLOR

-0.17

-0.2

0.084

-0.26

0.46

0.091

0.07

1

 

 

 

 

 

 

 

 

 

 

TURBIDITY

-0.12

-0.1

0.134

-0.05

0.38

0.083

0.3

0.898

1

 

 

 

 

 

 

 

 

 

Na+

-0.66

0.56

-0.19

-0.03

0.13

-0.35

-0.1

0.431

0.4203

1

 

 

 

 

 

 

 

 

K+

-0.61

0.37

-0.05

-0.09

0.09

-0.37

-0.4

0.315

0.1738

0.85

1

 

 

 

 

 

 

 

Ca+

-0.37

0.27

-0.02

0

0.27

-0.32

-0.1

0.479

0.6464

0.54

0.316

1

 

 

 

 

 

 

Mg+

-0.21

0.19

-0.14

-0.32

0.18

-0.47

-0.4

0.231

0.2606

0.44

0.314

0.769

1

 

 

 

 

 

TH

-0.36

0.27

-0.03

-0.03

0.27

-0.34

-0.2

0.464

0.6209

0.54

0.322

0.998

0.81

1

 

 

 

 

Cl- 

0.177

-0.3

-0.43

-0.21

0.01

-0.01

0.12

0.462

0.3261

-0

-0.1

0.183

0.16

0.18

1

 

 

 

SO

-0.31

0.34

0.21

0.53

-0.44

0.328

0.27

-0.22

-0.022

-0

-0.03

0.06

-0.26

0.03

-0.366

1

 

 

NO3-

-0.47

0.26

0.209

0.32

-0.09

0.086

0.06

0.488

0.5518

0.41

0.403

0.393

-0.08

0.35

0.0742

0.47

1

 

PO43-

-0.37

0.62

0.383

0.38

-0.04

-0.14

0.07

-0.34

-0.144

0.04

-0.12

0.263

0.29

0.27

-0.557

0.34

-0.15

1

 Table 24 –Correlation matrix among 16 parameters of industrial wastewater

Novelty of research

 The novelty of monitoring the concentration of lead in the industrial area of Balodabazar would depend on the specific details of the research and the methodology used. However, there could be several potential areas of novelty, such as:

 1.     Location: The specific industrial area in Balodabazar Chhattisgarh has not been studied before, so this research could provide valuable data on the lead concentration levels in that area.

 2.     Impact Assessment: The research could focus on assessing the impact of industrial activities on lead concentration in the environment, which could help identify potential pollution sources and develop strategies to mitigate their effects.

 3.     Novelty of Testing Methods: The research may use innovative techniques or methods to measure the lead concentration levels in the industrial area, such as advanced analytical methods, or AI-driven models to predict future levels of lead contamination.

 4.     Policy Implications: The research can help identify the potential policy gaps or limitations associated with lead contamination management. This could lead to the development of new policies to control the release of lead in the environment.

 Discussion

 The analysis of waste water for Lead contamination is an important step in ensuring human and environmental health safety. Excess levels of lead may cause short term and long term effects to human. The concentration of lead in 16 industrial wastewater samples.  The sample 11 has the highest content 8 has the lowest concentrations. The concentration of Lead in industrial effluent samples was found to vary significantly. The concentrations of Pb obtained were 0.4869, 0.3637, 0.3701, 0.5383, 0.5099, 0.3985, 0.4087, 0.3237, 0.4478, 0.4601, 0.5936, 0.4156, 0.4222, 0.4173, 0.4456 and 0.3596 respectively. The levels were above /below the maximum limit set by CPCB. The non detected levels of Pb could be due to its absence in raw materials in use at the time of sample collection.

 Conclusion

Waste water collected from cement industrial area was analyzed for the presence of Lead (heavy metal) and evaluation of physicochemical parameters. The result revealed the presence of elevated levels of lead higher as compared to CPCB standards. The study reveals that the industrial effluent analyzed was polluted with Lead which might have originated from the industrial processes. High sulphate level may corrode plumbing, particularly copper piping, the industrial effluent should therefore be monitored and properly treated before discharged to streams so as to safeguard the environment.

 Acknowledgement

I would like to express my profound gratitude and grateful regards to my supervisor,  Mr. Sudheer Bhoi, Guest Lecturer, School of Studies in Environmental Science, Pt. Ravishanka