Evaluation of Water Quality Pollution Indices for part of Bokaro District, Jharkhand

DOI : 10.17577/IJERTV5IS020629

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  • Authors : Sumanta Kumar Biswal, Vijay Laxmi Mohanta, Prasoon Kumar Singh, Poornima Verma
  • Paper ID : IJERTV5IS020629
  • Volume & Issue : Volume 05, Issue 02 (February 2016)
  • DOI : http://dx.doi.org/10.17577/IJERTV5IS020629
  • Published (First Online): 05-03-2016
  • ISSN (Online) : 2278-0181
  • Publisher Name : IJERT
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Evaluation of Water Quality Pollution Indices for part of Bokaro District, Jharkhand

Sumanta Kumar Biswal, Vijay Laxmi Mohanta , Poornima Verma , Prasoon Kumar Singh

Department of Environmental Science and Engineering, Indian School of mines, Dhanbad-826004, Jharkhand, India

Abstract – Bokaro is a hub of mining, industries, wholesale trade and commerce. Due to rapid industrialization and mining activity many environmental problems like air pollution, subsidence, damage to the aquifer, accelerated soil erosion and destruction of soil structure are rising. Therefore, degrading both the ground water and surface water quality, on which most of the population is dependent for drinking and other domestic purpose. 20 groundwater samples were collected from different locations in Bokaro district, Jharkhand. The dug-wells samples were analysed for various physiochemical parameters and 6 heavy metals including Copper, Iron, Manganese, Lead, Cadmium and Zinc. The contamination levels of 20 locations were evaluated using Contamination Index (Cd) and Heavy Metal Pollution Index (HPI). The result shows that the major heavy metal pollutants exceeding Bureau of Indian Standards (BIS) permissible limits are Copper, Manganese and Iron at various locations. The study recommends proper treatment and maintenance for the affected sites.

Keywords – Heavy Metal Pollution Index (HPI), Contamination Index (Cd), Heavy Metal, ground water, Bokaro.

  1. INTRODUCTION

    Water is available throughout the globe and it is a good solvent, which makes it highly vulnerable to pollution. Many a times, it is difficult to provide water of desired quantity and quality at a desired place. At times, enough water may be available but the quality may be so poor that it is of no use without treatment. Groundwater is a widely present natural source for irrigation, drinking, and other purposes of water requirements in many parts of India. More than 90 % of rural and nearly 30% of urban population depend on it for drinking water (NRSA 2008). Unfortunately, excessive use and continuous mismanagement of this vital resource led to clean water scarcity and ecosystem degradation (Tsakiris 2004; Jha et al., 2007; Aggarwal et al.,2009b; Rodell et al., 2009; Chawla et al., 2010). Heavy metals such as Zn, Cu, Pb, Cd, Ni, are present in these water may pose several threats to ecosystem safety and human health such as Kidney damage, Cancer, Nervous system degradation, etc. (Lashun et al., 2008; Vasudevan et al.,2011). Thus the comparative assessment, investigation and management of water quality resource is important. And in order to do so, it is necessary to evaluate the degrees of heavy metals contaminations to analyse present scenario and to take necessary action if required. However, the interpretation of data sets of several metals is complicated (Nasr et al., 2013). For the comparative purpose simplifying multivariate data to generate & a single value

    may be used (Miyai et al., 1985; Nimic & Moore, 1991). Several other methods such as fuzzy mathematics, membership degrees, factor analysis, gray modelling and hierarchy process are there for evaluation of water quality. Over the past four decades, several authors have developed a number of water quality indices (WQIs), employing various mathematical and statistical methods. Some of these methods have been implemented by water management and environmental agencies and are aiding decision-makers in water resources management, public health and ecosystem protection. One of the major advantage of WQI is that it incorporates data from multiple water quality parameters into a mathematical equation that rates the health of water quality with number (Yogendra, K and Puttaiah, 2008).

  2. DESCRIPTION OF STUDY AREA

Bokaro district of the Jharkhand is one of the most industrialized belt in India. It was established in 1991 by carving out one subdivision consisting of two blocks from Dhanbad District and six blocks from Giridih District. Bokaro Steel City is the district headquarters. Bokaro is famous for its Steel Plant which is the biggest in Asia. It is one of the highly industrialized coal belt districts in Jharkhand. Bokaro district is bounded by Giridih in the north, purulia (West Bengal) in the South, Dhnabad in the East and Hazaribagh in the West.

The district is spreaded over 2861 sq. km lying between latitude 2302427 E to 2305724 E and Longitude 8503430 N to 8602910 N. The district headquarters is at Chas. The district comprises of two sub-divisions i.e. Chas and Bermo with eight blocks namely Chas, Gomia, Nawadih, Bermo, Peterwar, Kasmar, Jaridih and Chandan kiyari. Geologically the Bokaro district is a part of Chhotanagpur Plateau. It is highly undulating and hilly all over the district. The regional slope of the district is towards east and controlled the alignment of the tributaries of Damodar River. Damodar Basin is the main basin of the district. Groundwater in the district is mainly replenished by the atmospheric precipitation. Influent seepages from canal, streams and other surface water bodies, also to contribute to the groundwater in the district. The hydrogeological condition of the district is very complicated due to vide variability of geology, topography, drainage and mining activity. The district also a mining belt of Parbatpur blocks in its South-East direction.

Fig. 1: Study Area / Sampling Locations in Bokaro District (DW)

II. MATERIAL AND METHODS

  1. Contamination index(Cd)

    Cd summarises the combined effects of several quality parameters considered harmful to household water. The contamination index is calculated from equation below,

    Contamination index summarized the combinational effects of several quality parameters, that may have harmful consequences to human health/the environment. The value scale for contamination index consists of 3 ranges; Cd< 1 (low contamination), 1 < Cd < 3 (medium contamination) and Cd > 3 (high contamination).

  2. Heavy metal pollution index (HPI)

The HPI represent the total quality of water with respect to heavy metals. The HPI is based on weighted arithmetic quality mean method and developed in two steps. First by establishing a rating scale for each selected parameter giving weightage and second by selecting the pollution parameter on which the index is to be based. The rating system is an arbitrarily value between zero to one and its selection depends upon the importance of individual quality considerations in a comparative way or it can be assessed by making values inversely proportional to the recommended standard for the corresponding parameter (Horton, 1965; Mohan et al., 1996). In computing the HPI, Prasad and Bose (2001) considered unit weightage (Wi) as a value inversely proportional to the recommended standard (Si) of the corresponding parameter as proposed by Reddy (1995).

The HPI model (Mohan et al., 1996) is given by:

Where;

Cfi= (CAi/CNi) 1

Cd=

Cd=

=1

Cfi= contamination factor for the i-th component CAi= analytical value for the i-th component CNi= upper permissible concentration of the

i-th component. (N denotes the normative value)

The sub-index (Qi) of the parameter is calculated by

Where, Mi = monitored value of heavy metal of ith parameter,

Ii = ideal value of the ith parameter

Si = standard value of the ith parameter.

The sign () indicates numerical difference of the two values, ignoring the algebraic sign. The critical pollution index of HPI value for drinking water as given by Pasad and Bose (2001) is 100.

IV. RESULTS AND DISCUSSIONS

The evaluation of the eight heavy metals Fe, Mn, Cu, Zn, Cd, Ni, Pb, Hg and other physical parameters from 20 locations (GW1-GW20) were calculated and analysed (Table I & II). Turbidity, Alkalinity, Total Hardness at several locations were found to be exceeding desirable limits.

where, Qi = sub-index of the ith parameter.

Wi = unit weightage of the ith parameter n=number of parameters considered.

Also the heavy metals concentration of all the 20 locations were analysed and was found that Iron concentration at most of the locations were exceeding the acceptable limits. Copper, Nickel, Manganese concentration at some locations were exceeding the desirable limits but was within the permissible limits.

While Mercury, Lead, Cadmium & Zinc was found within the range. It can be concluded that most of the pollution problems are due to iron concentration. Further, the Heavy Metal Pollution index was evaluated and was found that HPI value for all the locations lies far below the critical value ie.

100. The methods used to calculate Heavy Metal Pollution Index has been found to be very helpful to analyse and compare variations of all the selected samples. The Contamination index was calculated and it was found that several locations GW-7, GW-8, GW-10, GW-13, GW-14, GW-18, GW-19 was exceeding Cd value 3, showing high contamination degrees. While, at several locations GW-1, GW-2, GW-3, GW-4 GW-5, GW-12, GW-17, GW-20 the Cd value was below 1, showing least contamination.

Table I. Physico-chemical parameters at different sampling locations

Sample Code

Location

pH

EC

(µs/cm)

Turbidity (NTU)

TDS

Total Alkalinity

Cl

Ca

Mg

Na

K

Total hardness

GW-1

Jharna

7.66

450

2.7

282

212

120.6

92.3

11.8

63.5

3.6

280

GW-2

Bermo

6.98

530

9.2

374

76

32.5

57.6

23.3

44.2

3.5

240

GW-3

Dantu

7.51

630

10.3

269

77

20.2

32

21.8

15.9

2.1

170

GW-4

Kashi Jharia

7.32

750

5.7

482

138

39.6

39.9

24.9

24

5.6

202

GW-5

Dhandaber

7.6

490

6.2

364

179

75.8

75.5

43.2

45.1

6.5

366

GW-6

Siwandih

6.98

898

4.2

1059

212

58.4

96.3

33.1

36.6

3

378

GW-7

Gudkutarh

7.11

1455

0.8

1123

162

186.7

122.3

82

44.5

2.8

642

GW-8

Kalyanpur

7.32

892

4.2

550

539

200.1

106.2

56.6

25.3

10.1

498

GW-9

Mamkudar

6.97

574

1.4

386

302

69.7

76.3

65.9

55.6

3.2

461

GW-10

Bhawanipur

7.87

1518

2.3

1059

154

198.2

93.1

57.2

46.1

4

467

GW-11

Chadankiyari

7.21

1349

3.4

958

289

88.5

81.4

45.5

18.8

4.5

390

GW-12

Khasmahal

6.86

372

4.3

238

302

51.2

92.3

42.2

31.2

9.6

404

GW-13

Sitanalah

7.97

1274

6.9

1195

77

75.5

83.3

61.2

33.8

6.8

459

GW-14

Pidrajora

7.76

1178

2.3

792

378

154.2

70.1

68.7

51.7

9.7

457

GW-15

Tulbul

7.58

880

4.2

713

309

60.2

105.2

22.3

83

7.5

354

GW-16

Peterwar

7.63

1200

5.2

998

399

100.2

69.1

36.9

53.6

3.7

324

GW-17

Jainamore

6.92

750

2.9

586

345

49.2

68.7

37.2

24.4

6.3

325

GW-18

Telgaria more

7.02

1142

6.8

1040

375

58.5

44.2

55.2

34.7

4.55

337

GW-19

Baladih

7.68

879

6.2

682

212

150.2

103.2

52.5

43.7

7.5

473

GW-20

Khutari

6.66

381

6.4

220

155

52.8

39.2

51.4

25.1

3.5

309

All parameters are with unit mg/L unless specified.

Table II. Heavy metal concentration at different sampling locations

Sample Code

Location

Fe

Ni

Cu

Zn

Mn

Cd

Hg

Pb

GW-1

Jharna

992

10.1

4.1

200

190.3

0.2

0.3

0.65

GW-2

Bermo

1125

20.1

1

324

122.2

1.2

0.07

1.02

GW-3

Dantu

1201

12.3

1.2

165

69.9

0.2

0.3

1.96

GW-4

Kashi Jharia

998

10

1.3

62

82.3

0.3

0.8

0.32

GW-5

Dhandaber

789

12

3.8

67

69.8

0.6

0.05

0.19

GW-6

Siwandih

1100

3.9

2.8

72

231

0.3

0.06

0.29

GW-7

Gudkutarh

789

7.9

38.9

32

12.6

0.2

0.12

2.23

GW-8

Kalyanpur

1022

1.8

1.7

25

11.8

1.06

0.78

1.96

GW-9

Mamkudar

600

5.2

2.1

29

9.2

1.07

0.03

1.52

GW-10

Bhawanipur

621

6.2

1.2

87

27.3

0.03

0.04

0.32

GW-11

Chadankiyari

803

4.2

2.1

8

22.4

1.2

0.04

0.18

GW-12

Khasmahal

1056

8.2

1

15

95.1

1.09

0.21

0.95

GW-13

Sitanalah

756

11.5

2

45

9.2

0.04

0.16

0.12

GW-14

Pidrajora

856

26.8

2.9

22

25.3

0.02

0.14

0.01

GW-15

Tulbul

562

24.6

3.2

19

23.5

0.08

0.09

2.01

GW-16

Peterwar

486

10.2

1

11

62.1

0.6

0.19

1.35

GW-17

Jainamore

475

11.9

1

72

162.4

1.02

0.34

1.05

GW-18

Telgaria

702

19.5

51.3

300

215.3

0.44

0.01

1.38

GW-19

Baladih

635

5.3

0.8

229

201.3

0.32

0.78

0.98

GW-20

Khutari

365

9.6

3.1

69

56.8

0.21

0.42

0.84

All parameters are with unit µg/L.

4

Contamination Index

3

Contamination Index

Contamination Index

2

1

0

-1

-2

-3

Sampling Locations

High Contamination

Moderate Contamination

Cd

Low Contamination

Figure 2: Graphical Representation of degree of Contamination Index

120

100

80

HPI

HPI

60

40

20

0

Heavy Metal Pollution Index

Sampling Locations

HPI

Figure 3: Graphical Representation of Heavy Metal Pollution Index

CONCLUSION

We have analysed all the samples from 20 locations from Bokaro district and the areas are affected by mining & industrial activities. Though the heavy metal pollutions lie below the critical value of HPI but the Iron contamination is affecting the ground water severely day by day. So, the control of activities that causes Iron contamination is recommended. The Contamination Index(Cd) of 2 locations

i.e. Gudkutarh & Kalyanpur (Baru) are found to be highly contaminated.

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