ISSN : 0970 - 020X, ONLINE ISSN : 2231-5039
     FacebookTwitterLinkedinMendeley

Seasonable Variation on Trace Metals Statistical Values of Groundwater in and Around Tannery Areas of Vellore District

A. Kistan1* and V. Kanchana2 and N. K. Geetha3

1Panimalar institute of technology, Chennai – 123, India.

2Sree Sastha institute of Engineering and technology, Chennai – 123, India.

3Dayananda Sagar College of Engineering, Bangalore-560098, India.

Corresponding Author E-mail: vishmikrish@gmail.com

DOI : http://dx.doi.org/10.13005/ojc/370331

Article Publishing History
Article Received on : 21-Apr-2021
Article Accepted on : 24-May-2021
Article Published : 21 Jun 2021
Article Metrics
ABSTRACT:

This paper investigates the determination of seasonable variation of trace metals named Copper, Zinc, Iron, Cadmium, Chromium and Lead set down in the groundwater in and around area of tannery areas of Vellore district. The tanneries discharge untreated tannery effluents, which get mixed with the soil, water of the Palar River, and underground in this area. The determination of metals was performed for the groundwater samples which are collected from adjacent to tannery localities, which bears untreated tannery effluents at pre-monsoon and post-monsoon seasons. The metals might be deposited into the plants and vegetables grown on that agricultural soil, which disturb human health. Somewhat risky amount of trace metals were found in some groundwater samples, especially in the case of in pre-monsoon. All these trace metals were analysed by the Atomic adsorption spectroscopy technique (AAS). These metals contamination in the groundwater is answerable for the support of harmfulness in farming crops and underground water.

KEYWORDS:

AAS; Groundwater; Tannery; Trace metals; Vellore District

Download this article as: 

Copy the following to cite this article:

Kistan A, Kanchana V. Seasonable Variation on Trace Metals Statistical Values of Groundwater in and Around Tannery Areas of Vellore District. Orient J Chem 2021;37(3).


Copy the following to cite this URL:

Kistan A, Kanchana V. Seasonable Variation on Trace Metals Statistical Values of Groundwater in and Around Tannery Areas of Vellore District. Orient J Chem 2021;37(3). Available from: https://bit.ly/3cT3sJ2


Introduction

Over two third of earths surface is covered by water less than a third is taken up by land. On earth 96.5% of water is found in seas and oceans and the remaining is groundwater. Water plays an important role in the world economy because water is an excellent solvent for a wide variety of applications such as household, industries, and agriculture sectors. In earth, water moves continually through the water cycle of evaporation, transpiration, condensation and precipitation1. Safe drinking water is essential to humans and other life form even through it does not provide calories or organic nutrients. The lakes, streams and rivers water level will be change with respect to weather but the level of groundwater will not be changed but it decreases due to use of irrigation, domestic and industrial purpose and recharge after several years or months due to rains subsequently.

The groundwater chemistry is mainly controlled by the reactions of geochemical along the direction of flow. It is important to identify these geochemical reactions in the water in order to assess the distribution of major ions of the region2. In all living organism including human being to live in earth the basic need is water3.In rural areas most of the people are using groundwater for drinking purpose but groundwater is unfit for drinking purpose because it carries total dissolved solids this is due to various factors such as industrial waste, disposal of sewage etc.

In many cities of India usage of groundwater is increased including Vellore district due to over population, increased in industrial sector and agriculture, which decrease the groundwater level.     

At present, pollution of groundwater is a global environmental problem, due to over exploration and demand of groundwater resources and their recharging is reduced1-3. The trace metal contaminates in aquifers of groundwater as constitution of natural due to interaction of soil-water and chemical constituents movement4. An ecosystem of aquatic and groundwater contaminations in trace metals. Many researchers have been studied5-9 by the contaminations of trace metal in groundwater.  The natural process of leaching and precipitation is also susceptibly polluted in groundwater results erosion of soil and reduction of quality of water. At present study investigation of copper (Cu) zinc (Zn) iron (Fe) lead (Pb) chromium (Cr) and cadmium (VEL) content in groundwater in Vellore district.

Materials and Methods

The groundwater samples were collected in 2L pre cleaned polythene bottles. Add 1ml of con.HNO3 in each groundwater samples and filtered immediately using 0.45 µm membrane filter of millipore10 and stored at 40 C in laboratory. The hot plate used to digest the samples and volume reduces less than 50ml. It is poured in volumetric flash and made up 50 ml used in double distilled water11. These samples are kept in dark room and analyses the trace metal by atomic absorption spectrophotometer method 12.

Results and Discussion

Heavy metals are one of the toxic pollutants in groundwater. It was extracted from earth’s crust. Copper is one of the common trace metals, which enter into groundwater due to wastage of industries, copper pipes corrosion and pesticides used in agriculture. The human health need trace amount of copper but, but it concentration is high in drinking water cause damage of liver and kidney 13. The study area copper concentration varies from 0 to 2.25 ppm with average of 0.71 ppm, 0 to 1.33 ppm with average of 0.477 ppm and 0.04 to 1,94 ppm with average of 0.767 ppm and 0.19 to 2.82 ppm with average of 1.104 ppm in north, south, central and west parts of Vellore district respectively. The maximum copper concentration recorded is (N1, W4, W6, W8, W10) According to World health organization 15 samples exceeds in permissible limit (1 ppm). The zinc concentration varies between 0.36 to 2.84 ppm with average 1.39 ppm in north, 0.48 to 3.83 ppm with average 1.841 ppm in south, 0 to 3.28 ppm with average 1.39 ppm in central and 0.1 to 2.27 ppm with average 1.224 ppm in west part in Vellore district, which enters into groundwater from galvanic industries, productions of battery, zinc pipes and paints. The concentration of zinc is increased may cause stomach ache, fever, diarrhea and vomiting14. In our study area all the samples were not exceed in BSI standards and worlds health organization. Iron is one of the essential trace metals in our body. It enters into water from ore, pipes corrosion, etc.. The iron concentration ranges from 0 to 1.5ppm with average 0.481ppm in north, 0.04 to 2.17ppm with average 0.579ppm in south, 0 to 0.76ppm with average 0.205ppm in central and 0.02 to 2.17ppm with average 0.608ppm in west part of Vellore district. 44% of the samples are exceeds the permissible limit (0.3ppm) the maximum ion concentration was recorded in (S7). Lead is one of the toxic trace naturally occurring metals. The lead concentration may increase in environmental due to many human activities. Lead concentration varies between 0 to 0.38 ppm with average of 0.008 ppm, 0 to 0.0038 ppm with average of 0.006 ppm and 0. to 0.019 ppm with average of 0.004ppm and 0.002 to 0.076 ppm with average of 0.018 ppm in north, south, central and west parts of Vellore district respectively. The drinking water contains small content of lead it cause 15 blood pressure, damage of kidney etc. The present study areas most of samples within the desirable limit except W9 and W10 based on standards of ISI and WHO.  The groundwater contains cadmium may naturally or contaminated from mining, sewage water, fertilizers and effluents of industries 16. It may be change in groundwater pH level. The cadmium concentration varies between 0 – 0.05 ppm in north, 0-0.005 ppm in south, 0-0.004 ppm in central and 0-0.006 ppm in west part of Vellore district. Based on WHO and BIS all the samples within the desirable limit (<0.01 ppm). The presence of chromium in groundwater naturally but it exists in combined state. It causes cancer and respiration system damage 17. All the samples are within desirable limit based on WHO and BIS.

Table 1: Trace metals statistical values of groundwater in north part of Vellore district

Sample Code

Copper

Zinc

Iron

Lead

Cadmium

Chromium

N1

2.25

2.84

0.99

0.003

0.002

0.038

N2

0.67

1.03

0.48

0.01

0.003

0.004

N3

0.57

1.35

0.08

0.038

0.004

0.003

N4

0.48

0.99

0.38

0.019

0.005

0.004

N5

0.04

0.99

0.57

0.003

0.002

0.002

N6

0.97

1.12

0.09

0.003

0.002

0.003

N7

1.52

1.79

0.05

0.009

0.001

0.001

N8

0.48

0.88

0.29

0.004

0.002

0.002

N9

1.18

0.88

1.26

0.004

0.002

0.001

N10

0.06

1.94

0.57

0

0.001

0.001

N11

0

0.36

0.02

0.002

0

0.002

N12

0.57

2.50

1.50

0.004

0.001

0.010

N13

1.33

1.94

0

0.005

0.002

0.002

N14

0.19

0.99

0.38

0

0.004

0.002

N15

0.04

1.39

0.48

0.001

0

0.001

N16

0.08

0.87

0.02

0.004

0.002

0.001

Minimum

0

0.36

0

0

0

0.001

Maximum

2.25

2.84

1.5

0.038

0.005

0.038

Mean

0.704

1.39

0.481

0.008

0.002

0.006

Units =  mgL-1 (ppm)

Table 2: Trace metals statistical values of groundwater in south part of Vellore district

Sample Code

Copper

Zinc

Iron

Lead

Cadmium

Chromium

S1

1.33

2.02

0.57

0.005

0.005

0.019

S2

1.33

1.89

0.04

0.038

0.003

0

S3

0.76

2.17

0.38

0.001

0.001

0.001

S4

0.47

1.12

0.19

0

0.004

0.002

S5

0.04

1.45

0.09

0.002

0.004

0.001

S6

0.38

2.34

1.2

0.002

0

0.010

S7

0.38

2.55

2.17

0.003

0

0.010

S8

0.02

0.48

0.08

0

0.001

0.001

S9

0

0.97

0.08

0.001

0.001

0.001

S10

0.97

1.73

0.76

0.004

0.001

0.002

S11

0.04

1.89

0.57

0.002

0.004

0.004

S12

0.76

3.83

0.51

0.004

0.002

0.002

S13

0.29

1.50

0.19

0.002

0.001

0.002

S14

0.19

1.39

0.06

0.001

0.002

0.002

S15

0.01

1.89

0.76

0.001

0.002

0.002

S16

0.29

1.6

0.57

0.002

0.004

0.002

Minimum

0

0.48

0.04

0

0

0

Maximum

1.33

3.83

2.17

0.038

0.005

0.019

Mean

0.477

1.841

0.579

0.0059

0.002

0.004

Units =  mgL-1 (ppm)

Table 3: Trace metals statistical values of groundwater in central part of Vellore district

Sample Code

Copper

Zinc

Iron

Lead

Cadmium

Chromium

C1

0.67

0.48

0.38

0.002

0.002

0.004

C2

1.07

1.33

0.01

0.001

0.002

0.001

C3

1.94

0.76

0.01

0.002

0.002

0.001

C4

0.76

1.07

0.76

0.004

0.001

0.001

C5

0.48

0.97

0.19

0.019

0.001

0.003

C6

0.38

0

0.01

0

0.002

0

C7

0.19

0.88

0.01

0.001

0

0.001

C8

0.19

0.02

0

0

0.001

0.001

C9

0.38

1.38

0.57

0.001

0.001

0.002

C10

1.18

0.34

0.04

0.002

0.002

0.001

C11

1.28

2.78

0

0.005

0.003

0.002

C12

1.14

2.23

0.76

0.004

0.002

0.002

C13

0.97

1.73

0

0.002

0.002

0.001

C14

0.04

2.55

0

0.004

0

0.002

C15

0.67

1.89

0.19

0.004

0.003

0.004

C16

0.48

3.28

0

0.006

0.004

0.006

Minimum

0.04

0

0

0

0

0

Maximum

1.94

3.28

0.76

0.019

0.004

0.006

Mean

0.7667

1.387

0.205

0.004

0.0018

0.002

 Units =  mgL-1 (ppm)

Table 4: Trace metals statistical values of groundwater in west part of Vellore district

Sample Code

Copper

Zinc

Iron

Lead

Cadmium

Chromium

W1

0.19

1.01

0.38

0.004

0.001

0.002

W2

0.38

0.57

1.07

0.002

0

0.010

W3

0.48

1.18

0.05

0.004

0.002

0.002

W4

2.82

1.83

2.17

0.002

0

0.010

W5

0.38

0.97

0.10

0.002

0.002

0.010

W6

2.13

1.89

0.97

0.019

0.004

0.002

W7

0.93

1.18

0.76

0.019

0.006

0.001

W8

2.36

1.41

0.06

0.010

0.004

0.002

W9

0.69

1.18

1.09

0.076

0.004

0.004

W10

2.30

2.27

0.57

0.057

0.002

0.005

W11

0.57

1.60

0.06

0.002

0

0.002

W12

0.48

0.72

0.02

0.002

0.004

0

W13

0.57

1.30

0.04

0.002

0

0

W14

0.38

0.10

0.19

0.002

0.001

0.019

Minimum

0.19

0.1

0.02

0.002

0

0

Maximum

2.82

2.27

2.17

0.076

0.006

0.019

Mean

1.104

1.224

0.608

0.0176

0.002

0.006

 Units =  mgL-1 (ppm)

Seasonal Analysis

The table 5.6,7 shows physic-chemical characteristic of groundwater in various seasons. The copper concentration increases from pre-monsoon to monsoon and further increase post monsoon. The maximum copper value were recorded in VEL47 (2.48ppm) in pre-monsoon, VEL46 (2.72ppm) in monsoon and post monsoon (2.84ppm). According to World health organization 31% of the samples exceeds in permissible limit in pre-monsoon and monsoon, 21% of the samples exceeds in  post monsoon (>1ppm).

The concentration of zinc ranging from 0.1 – 4.02ppm with average 1.58ppm in pre- monsoon, 0.2 to 3.62ppm with average 1.65ppm in monsoon, and
0.24 – 3.12ppm with average 1.41ppm in post monsoon. The zinc values decreases from pre-monsoon to monsoon and further decrease in post-monsoon. According to WHO all the groundwater samples are within the desirable limit (5ppm). The maximum values recorded in (VEL24) in pre-monsoon, the minimum values recorded in VEL52 in pre-monsoon, VEL9 in monsoon and post-monsoon.

The observer values of iron ranging from 0.001 – 2.28ppm with average 0.42 in pre- monsoon, 0.002 – 3.62ppm with average 0.435ppm in monsoon and
0.001 – 2.18ppm with average 0.352ppm in post-monsoon. The iron concentration gradually increases from pre- monsoon to monsoon and decreases in post-monsoon. The iron permissible limit in drinking water is 0.1ppm prescribed by BIS, but 8 samples exceed the permissible limit in pre monsoon, monsoon and post post-monsoon period. Hence this type of groundwater drawn from bore well is clean but after sometimes the cloudy and brown colour, due to Fe(OH)2 is precipitated18. The sampling site of VEL19 is recorded with maximum concentration in pre monsoon and monsoon periods.

The lead concentration is varies from 0.001 to 0.08ppm with average 0.08ppm, 0.01 to 0.08ppm with average 0.008 and 0.001 to 0.04ppm with average 0.005ppm in pre monsoon, monsoon and post monsoon respectively. The lead concentration may constant in pre monsoon and monsoon but it decrease in post monsoon. All samples in three seasons within the desirable limit (< 0.05ppm). Cadmium is one of the hazardous metal in environment, because greater accumulation and high toxicity. The range of cadmium is 0.001 – 0.005ppm with average 0.002ppm in pre monsoon and monsoon, 0.001 – 0.004ppm with average 0.002ppm in post monsoon. Almost all the groundwater samples within the desirable limit (<0.005ppm) based on World health organization. The chromium concentration varies from 0.001 to 0.04ppm with average 0.004ppm in pre-monsoon, 0.001 – 0.002ppm with average 0.005ppm in monsoon and 0.001 to 0.01ppm with average 0.004ppm in post-monsoon, the chromium concentration gradually decrease from pre-monsoon to post-monsoon.

Table 5: Trace metals statistical values of groundwater in Vellore district at pre-monsoon

Sample Code

Copper

Zinc

Iron

Lead

Cadmium

Chromium

VEL1

2.36

2.98

1.04

0.004

0.002

0.04

VEL2

0.7

1.08

0.5

0.01

0.003

0.004

VEL3

0.6

1.42

0.08

0.04

0.004

0.003

VEL4

0.5

1.04

0.4

0.02

0.005

0.004

VEL5

1.02

1.18

0.1

0.003

0.002

0.003

VEL6

0.5

0.92

0.3

0.004

0.002

0.002

VEL7

1.24

0.92

1.32

0.004

0.002

0.001

VEL8

0.06

2.04

0.6

Nil

0.001

0.001

VEL9

0

0.38

0.02

0.002

Nil

0.002

VEL10

0.6

2.62

1.58

0.004

0.001

0.01

VEL11

1.4

2.04

0.005

0.005

0.002

0.002

VEL12

0.2

1.04

0.4

Nil

0.004

0.002

VEL13

0.08

0.92

0.02

0.004

0.002

0.001

VEL14

1.4

2.12

0.6

0.005

0.005

0.02

VEL15

1.4

1.98

0.04

0.04

0.003

Nil

VEL16

0.8

2.28

0.4

0.001

0.001

0.001

VEL17

0.04

1.52

0.09

0.002

0.004

0.001

VEL18

0.4

2.46

1.26

0.002

Nil

0.01

VEL19

0.4

2.68

2.28

0.004

Nil

0.01

VEL20

0.02

0.5

0.08

Nil

0.001

0.001

VEL21

0

1.02

0.08

0.001

0.001

0.001

VEL22

1.02

1.82

0.8

0.004

0.001

0.002

VEL23

0.04

1.98

0.6

0.002

0.004

0.004

VEL24

0.8

4.02

0.54

0..004

0.002

0.002

VEL25

0.3

1.58

0.2

0..002

0.001

0.002

VEL26

0.2

1.46

0.06

0.001

0.002

0.002

VEL27

0.3

1.68

0.6

0.002

0.004

0.002

VEL28

0.7

0.5

0.4

0.002

0.002

0.004

VEL29

1.12

1.4

0.01

0.001

0.002

0.001

VEL30

2.04

0.8

0.01

0.002

0.002

0.001

VEL31

0.8

1.12

0.8

0.004

0.001

0.001

VEL32

0.5

1.02

0.2

0.02

0.001

0.003

VEL33

0.2

0.92

0.01

0.001

Nil

0.001

VEL34

0.4

1.45

0.6

0.001

0.001

0.002

VEL35

1.24

0.36

0.04

0.002

0.002

0.001

VEL36

1.34

2.92

0.003

0.005

0.003

0.002

VEL37

1.2

2.34

0.8

0.004

0.002

0.002

VEL38

1.02

1.82

0.002

0.002

0.002

0.001

VEL39

0.04

2.68

0.004

0.004

Nil

0.002

VEL40

0.7

1.98

0.2

0.004

0.003

0.004

VEL41

0.5

3.44

0.001

0.006

0.004

0.006

VEL42

0.2

1.06

0.4

0.004

0.001

0.002

VEL43

0.4

0.6

1.12

0.002

Nil

0.01

VEL44

0.5

1.24

0.05

0.004

0.002

0.002

VEL45

0.4

1.02

0.1

0.002

0.002

0.009

VEL46

2.24

1.98

1.02

0.02

0.004

0.002

VEL47

2.48

1.48

0.06

0.01

0.004

0.002

VEL48

0.72

1.24

1.14

0.08

0.004

0.004

VEL49

2.42

2.38

0.6

0.06

0.002

0.005

VEL50

0.6

1.68

0.06

0.002

Nil

0.002

VEL51

0.5

0.76

0.02

0.002

0.004

Nil

VEL52

0.4

0.1

0.2

0.002

0.001

0.02

Minimum

0.001

0.1

0.001

0.001

0.001

0.001

Maximum

2.48

4.02

2.28

0.08

0.005

0.04

Mean

0.7509

1.5763

0.4200

0.0084

0.0024

0.0044

Units =  mgL-1 (ppm)

Table 6: Trace metals statistical values of groundwater in Vellore district at monsoon

Sample Code

Copper

Zinc

Iron

Lead

Cadmium

Chromium

VEL1

2.48

3.32

1.12

0.005

0.001

0.02

VEL2

0.8

1.84

0.6

0.01

0.005

0.008

VEL3

0.7

1.62

0.08

0.02

0.003

0.006

VEL4

0.8

1.28

0.2

0.02

0.005

0.009

VEL5

1.04

1.26

0.1

0.008

0.003

0.004

VEL6

0.6

1.12

0.9

0.002

Nil

0.001

VEL7

1.18

0.88

1.24

0.004

0.001

0.002

VEL8

0.04

1.88

0.4

0.001

Nil

0.001

VEL9

0.01

0.2

0.02

Nil

Nil

Nil

VEL10

0.5

2.38

1.56

0.003

0.001

0.01

VEL11

1.4

2.68

0.008

0.008

0.004

0.002

VEL12

0.3

1.44

0.5

0.001

0.002

0.004

VEL13

0.05

1.02

0.04

0.002

0.002

0.001

VEL14

1.8

2.2

0.7

0.006

0.005

0.01

VEL15

1.2

1.86

0.08

Nil

0.002

Nil

VEL16

0.8

2.14

0.4

0.002

0.002

0.001

VEL17

0.04

1.82

0.09

0.001

Nil

0.001

VEL18

0.5

2.28

1.26

0.004

0.001

0.01

VEL19

0.5

2.32

1.88

0.004

0.001

0.02

VEL20

0.01

0.9

0.08

Nil

Nil

Nil

VEL21

0.09

1.02

0.09

0.001

0.001

0.001

VEL22

1.08

1.24

0.4

0.002

0.001

0.001

VEL23

0.09

1.88

0.6

0.001

0.001

0.001

VEL24

0.8

2.16

0.4

0.002

0.003

0.003

VEL25

0.6

1.48

0.2

0.001

0.002

0.001

VEL26

0.2

1.12

0.09

Nil

0.001

Nil

VEL27

0.4

1.54

0.6

0.001

0.001

Nil

VEL28

0.8

0.62

0.9

0.001

0.004

0.004

VEL29

1.18

1.2

0.01

Nil

0.002

Nil

VEL30

1.4

0.86

0.07

Nil

0.004

Nil

VEL31

0.8

1.24

0.4

Nil

0.002

Nil

VEL32

0.6

1.14

0.5

0.001

0.001

0.005

VEL33

0.2

1.02

0.04

Nil

Nil

Nil

VEL34

0.6

1.44

0.8

0.001

0.001

0.001

VEL35

Nil

0.8

0.06

Nil

Nil

Nil

VEL36

1.6

2.86

0.005

0.005

0.002

0.002

VEL37

1.08

2.88

0.8

0.005

0.001

0.002

VEL38

1.2

1.98

0.002

0.002

0.002

0.001

VEL39

0.04

2.24

0.004

0.004

0.001

Nil

VEL40

0.8

2.26

0.2

0.002

0.005

0.004

VEL41

0.2

3.62

0.008

0.002

0.004

0.002

VEL42

0.3

1.04

0.4

0.001

0.002

0.001

VEL43

0.4

1.12

1.18

0.002

0.002

0.01

VEL44

0.6

1.42

0.06

0.004

0.002

0.004

VEL45

0.4

1.28

0.1

0.01

0.002

0.01

VEL46

2.72

2.46

1.26

0.03

0.002

0.02

VEL47

2.4

1.72

0.06

0.01

0.003

0.002

VEL48

1.8

1.42

1.04

0.06

0.005

0.004

VEL49

2.24

2.68

0.6

0.08

0.003

0.006

VEL50

0.7

1.62

0.08

0.004

Nil

0.002

VEL51

0.92

0.92

0.02

0.02

0.004

Nil

VEL52

0.2

1.24

0.4

0.001

0.001

Nil

Minimum

0.01

0.2

0.002

0.001

0.001

0.001

Maximum

2.72

3.62

1.88

0.08

0.005

0.02

Mean

0.8076

0.2

0.4353

0.0082

0.0023

0.005

Units =  mgL-1 (ppm)

Table 7: Trace metals statistical values of groundwater in Vellore district at post-monsoon

Sample Code

Copper

Zinc

Iron

Lead

Cadmium

Chromium

VEL1

2.28

2.82

1.02

0.002

0.001

0.01

VEL2

0.6

1.05

0.4

0.009

0.002

0.002

VEL3

0.5

1.12

0.05

0.01

0.002

0.002

VEL4

0.5

1.02

0.1

0.01

0.002

0.003

VEL5

0.9

1.16

0.09

0.002

0.001

0.002

VEL6

0.4

0.82

0.2

0.002

Nil

0.001

VEL7

1.08

0.82

1.02

0.002

Nil

0.001

VEL8

0.042

1.82

0.5

Nil

Nil

Nil

VEL9

0.001

0.24

0.01

0.001

Nil

Nil

VEL10

0.4

2.14

1.55

0.003

Nil

0.009

VEL11

1.2

1.88

0.004

0.001

0.001

0.001

VEL12

0.1

1.02

0.2

Nil

0.001

0.001

VEL13

0.04

0.86

0.01

0.002

0.002

Nil

VEL14

1.2

2.04

0.5

0.004

0.004

0.01

VEL15

0.9

1.76

0.02

Nil

0.001

Nil

VEL16

0.6

2.04

0.2

Nil

0.002

Nil

VEL17

0.03

1.22

0.08

0.001

Nil

Nil

VEL18

0.3

2.18

1.06

0.001

Nil

0.008

VEL19

0.2

2.04

1.68

0.002

Nil

0.009

VEL20

Nil

0.4

0.03

Nil

Nil

Nil

VEL21

Nil

0.98

0.07

Nil

Nil

Nil

VEL22

0.09

1.22

0.3

0.001

Nil

Nil

VEL23

0.03

1.86

0.4

Nil

0.001

0.001

VEL24

0.5

2.06

0.3

0.002

0.001

0.001

VEL25

0.2

1.38

0.1

Nil

0.002

Nil

VEL26

0.1

1.02

0.04

Nil

Nil

Nil

VEL27

0.2

1.52

0.5

Nil

Nil

Nil

VEL28

0.6

0.4

0.2

Nil

0.001

0.003

VEL29

1.02

0.9

0.009

Nil

0.001

Nil

VEL30

1.28

0.6

0.009

Nil

0.001

Nil

VEL31

0.6

0.98

0.1

Nil

Nil

Nil

VEL32

0.4

0.82

0.1

Nil

Nil

0.002

VEL33

0.1

0.82

0.02

Nil

Nil

Nil

VEL34

0.4

1.34

0.6

Nil

Nil

Nil

VEL35

Nil

0.3

0.03

Nil

Nil

Nil

VEL36

1.24

2.82

0.002

0.004

0.002

0.001

VEL37

0.9

1.92

0.6

0.002

0.001

0.001

VEL38

0.98

1.78

0.001

0.001

0.001

Nil

VEL39

0.02

2.04

0.002

0.002

Nil

Nil

VEL40

0.7

1.98

0.1

0.001

0.002

0.002

VEL41

0.1

3.12

0.002

0.001

0.001

0.001

VEL42

0.1

1.04

0.2

0.001

Nil

0.001

VEL43

0.3

0.92

1.08

0.001

Nil

0.009

VEL44

0.4

1.22

0.04

0.002

0.001

0.001

VEL45

2.84

1.84

2.18

0.001

Nil

0.009

VEL46

2.02

1.98

0.98

0.01

0.002

0.009

VEL47

2.2

1.42

0.04

0.009

0.001

0.001

VEL48

0.68

1.12

1.02

0.04

0.002

0.002

VEL49

1.98

2.24

0.4

0.04

0.001

0.004

VEL50

0.5

1.62

0.05

0.002

Nil

0.001

VEL51

0.5

0.72

0.01

0.001

0.002

Nil

VEL52

0.1

0.98

0.1

Nil

Nil

Nil

Minimum

1.412

0.001

0.352

0.001

0.001

0.001

Maximum

3.12

2.18

2.18

0.04

0.004

0.01

Mean

0.24

0.001

0.001

0.0052

0.0015

0.0036

Units =  mgL-1 (ppm)

Table 8: Heavy metal Pollution Index (HPI) and Metal Index (MI) estimation for groundwater samples from Vellore district.

Sample Code

Pre-monsoon

Monsoon

Post-monsoon

HPI

MI

HPI

MI

HPI

MI

VEL1

104.0

0.780

108.19

0.737

108.71

0.607

VEL2

99.43

0.309

90.30

0.397

101.25

0.248

VEL3

91.59

0.339

98.96

0.285

104.87

0.177

VEL4

89.22

0.325

89.75

0.361

104.73

0.188

VEL5

105.88

0.253

100.70

0.294

110.49

0.208

VEL6

105.16

0.197

113.09

0.272

114.60

0.119

VEL7

103.06

0.487

107.70

0.450

112.90

0.369

VEL8

109.40

0.153

114.23

0.101

114.15

0.111

VEL9

114.89

0.021

115.18

0.007

115.06

0.008

VEL10

106.84

0.456

107.00

0.430

111.47

0.389

VEL11

105.92

0.314

96.55

0.364

110.92

0.245

VEL12

96.49

0.185

105.11

0.199

110.34

0.081

VEL13

105.69

0.077

105.92

0.070

105.98

0.058

VEL14

91.16

0.524

90.89

0.578

95.96

0.190

VEL15

96.37

0.445

106.41

0.267

110.95

0.190

VEL16

109.95

0.249

105.33

0.267

106.01

0.189

VEL17

96.87

0.115

114.93

0.049

144.93

0.035

VEL18

112.27

0.344

107.53

0.382

112.83

0.281

VEL19

109.71

0.523

106.14

0.519

111.27

0.373

VEL20

110.58

0.042

115.06

0.025

115.16

0.009

VEL21

110.44

0.048

110.44

0.065

115.08

0.023

VEL22

168.60

0.360

109.85

0.287

114.45

0.082

VEL23

95.74

0.215

109.32

0.159

109.90

0.112

VEL24

104.77

0.321

100.85

0.291

109.95

0.183

VEL25

110.11

0.131

105.85

0.190

106.12

0.099

VEL26

106.07

0.103

110.61

0.077

115.17

0.035

VEL27

95.79

0.249

109.39

0.204

114.18

0.134

VEL28

105.26

0.242

95.36

0.374

110.44

0.164

VEL29

106.40

0.244

106.55

0.245

110.98

0.198

VEL30

106.46

0.394

97.51

0.321

111.04

0.238

VEL31

108.60

0.312

105.59

0.247

115.16

0.128

VEL32

107.58

0.221

109.65

0.233

115.11

0.099

VEL33

115.12

0.052

115.20

0.051

115.21

0.029

VEL34

109.38

0.209

108.99

0.273

114.00

0.182

VEL35

106.19

0.261

115.10

0.019

115.15

0.008

VEL36

101.46

0.330

105.99

0.356

106.05

0.288

VEL37

104.25

0.413

108.56

0.385

109.37

0.298

VEL38

106.26

0.234

106.31

0.266

110.87

0.203

VEL39

114.71

0.057

110.2

0.062

114.98

0.033

VEL40

100.98

0.249

92.35

0.295

106.11

0.199

VEL41

96.65

0.228

97.14

0.155

110.69

0.075

VEL42

109.35

0.148

105.32

0.168

114.67

0.068

VEL43

112.54

0.300

103.46

0.349

112.75

0.274

VEL44

105.73

0.159

105.73

0.186

110.49

0.114

VEL45

105.87

0.165

104.74

0.198

110.92

0.890

VEL46

92.75

0.705

99.87

0.891

103.17

0.617

VEL47

96.37

0.546

100.84

0.519

109.92

0.439

VEL48

83.54

0.670

82.41

0.786

98.46

0.469

VEL49

96.99

0.780

89.63

0.840

104.66

0.585

VEL50

114.98

0.142

114.67

0.168

114.98

0.120

VEL51

97.115

0.168

94.65

0.300

106.23

0.130

VEL52

110.10

0.1911

109.78

0.138

115.04

0.044

 

Table 9: Correlation co-efficient matrices of trace metals with seasons Pre-monsoon

TRACE METAL

Cu

Zn

Fe

Pb

VEL

Cr

Cu

1.000

   

 

   

Zn

0.257

1.000

       

Fe

0.053

0.314

1.000

 

   

Pb

0.311

0.076

-0.070

1.000

   

VEL

0.261

0.081

-0.115

0.299

1.000

 

Cr

-0.071

-0.243

-0.066

-0.078

-0.190

1.000

Monsoon

TRACE METAL

Cu

Zn

Fe

Pb

VEL

Cr

Cu

1.000

 

 

     

Zn

0.402

1.000

 

     

Fe

0.224

0.224

1.000

 

   

Pb

0.528

0.199

0.169

1.000

   

VEL

0.433

0.179

-0.077

0.390

1.000

 

Cr

0.421

0.410

0.667

0.256

0.159

1.000

Post-monsoon

TRACE METAL

Cu

Zn

Fe

Pb

VEL

Cr

Cu

1.000

 

 

     

Zn

0.370

1.000

       

Fe

0.168

0.318

1.000

 

   

Pb

0.393

0.129

0.224

1.000

 

 

VEL

0.406

0.245

-0.102

0.303

1.000

 

Cr

0.335

0.350

0.711

0.163

0.198

1.000

 

Correlation Studies

Table. 9 shows correlation analysis of heavy metals in pre-monsoon, monsoon and post-monsoon seasons. During pre-monsoon the correlation between heavy metals didnt considerable because the value is very low but in monsoon season a moderately  correlated between the metals Cu-Pb (r=0.528) and strongly correlated between the metals Fe-Cr (r=0.667) and also strongly correlated in  post-monsoon season Fe-Cr (r=0.711). This is due to heavy metals may be dissoluted.

Heavy Metal Pollution Index and Metal Index

The total water quality of groundwater is represented by heavy metal pollution index 19 (HPI). The metal index value used to determine suitable for drinking purpose in groundwater.  Table 8 shows HPI and MI values in all urban areas of Vellore district.  In the study area 71%, 75% and 90% of groundwater samples exceeds the critical index values 100 in pre-monsoon, monsoon and post-monsoon respectively. This is due to trace metals leaching from pigments, fertilizers, etc. Based on MI classification 40% of samples are pure and 60% of samples are very pure in pre-monsoon, 35% of samples are pure and 65% of the samples are very pure in monsoon and 17% of samples are pure and 83% of the samples are very pure in post-monsoon.

Table 10: Correlation between variables and factor in Vellore district

Heavy Metals

Pre-monsoon

Monsoon

Post-monsoon

 

F1

F2

F1

F2

F1

F2

Cu

0.362

0.154

0.070

0.363

0.018

0.406

Zn

0.033

0.540

0.221

0.118

0.207

0.163

Fe

-0.228

0.535

0.509

-0.200

0.526

-0.179

Pb

0.450

-0.076

-0.031

0.386

-0.016

0.344

VEL

0.458

-0.076

-0.202

0.473

-0.185

0.493

Cr

-0.134

-0.276

0.451

-0.033

0.450

-0.025

Eigen value

1.775

1.351

2.584

1.368

2.440

1.365

Variability (%)

29.589

22.520

43.073

22.807

40.673

22.742

Cumulative %

29.589

52.109

43.073

65.880

40.673

63.415

Eigen values and two principal components values were extracted greater than 1 in all seasons. During pre-monsoon season, factor 2 moderately loaded with Zn and Fe, In monsoon season, factor 1 moderately loaded with Fe and post monsoon season also moderately loaded with Fe in factor 1 (table 10), which explain 30%, 52% and 40% of the variability in pre-monsoon, monsoon and post-monsoon seasons respectively of the data set.

During pre-monsoon season factor 2 moderately loaded with Fe and Zn. In monsoon and post monsoon seasons factor 1 moderately loaded with Fe. The groundwater contains trace amount of lead, cadmium and chromium this is due to metal dissolution during recharge of aquifer by rainfall.

Figure 1: First two principle components in pre-monsoon.

Click here to View figure

Figure 2: First two principle components in monsoon.

Click here to View figure

Figure 3: First two principle components in post-monsoon

Click here to View figure

Conclusion

The overall analysis of trace heavy metals in groundwater in and around Vellore district, they suggest following conclusions. The copper concentration of study areas, 33% of the samples exceeds in permissible limits. Iron concentration, 8 samples exceed permissible limits based on BIS. Lead concentration within the desirable limit in all three seasons.

In correlation analysis, monsoon and post-monsoon periods were moderately correlated between Cu-Pb and Fe-Cr.The study of principle component analysis shows moderately loaded in pre- monsoon, monsoon and post-monsoon seasons. This is due to dissolution of heavy metals, the effect of recharge in rain water and degradation of microbial by organic matter presence from wastewater. Heavy Metal Pollution Index (HPI) and Metal Index (MI) values in most of the samples were pure and very pure.

References

  1. Claxton. L.D, Houk. V.S, and Hughes. T.J, (1998), Mutat. Res., 410 (3), 237–43.
    CrossRef
  2. White. P.A, Rasmussen. J.B, (1998), Mutat. Res.,410(3), 223–36.
  3. White. P.A, Rasmussen. J.B. Blaise, C, (1996), Environ. Mol. Mutag., 27(2),140–151.
  4. Solomons. W, Forstner. U, (1984), Metals in the hydrocycle Berlin, Springer, 653.
    CrossRef
  5. Turekian. K.K, (1969), The oceans, streams and atmosphere, Berlin pringer, 468 (1969)
    CrossRef
  6. Lenvik. K, Steinnes. E, (1978), Pappas AC, Nord Hydrol.,9,197-206.
    CrossRef
  7. Borg. H, Johansson. K, (1989), Water, Air Soil, Pollut,.47, 427-40.
    CrossRef
  8. Runnels. D.C, Shepherd. T.A, and Angino. E.A, (1992), Env. Sci. Tech.,
    26, 2316-23.
  9. Gadh. R, Tandon. S.N, Mathur. R.P, Singh. O.V, (1993), Sci. Total Env., 136, 229-42.
  10. Vanmathi. G, and Gobalakrishnan. S, (1999), Indian J. Environ.Protect. 20, (6) 447-451.
  11. Prasad. B, and Bose. JM, (2001), Environ.Geol., 41, 183-88, (2001).
    CrossRef
  12. APHA, (1998), 3111, ‘Metals by flame atomic absorption spectrometry’, Clesceri, L.S., Greenberg, A.E., Eaton, A.D. (Eds.), Standard Methods for the Examination of Water and Wastewater, twentieth ed. American Public Health Association, Washington, DC, pp. 3-13e3-22.
  13. Kavitha.R and Elangovan. K (2010), Review article on groundwater quality characteristics at Erode district, India of Indian J. Environ. Sci., 1(2).
  14. Wang.J.S, Huang.P.M, Liaw.W.K, and Hammer.U.T, (1991), Kinetics of the desorption of mercury from selected freshwater sediments as influenced by chloride, Water, Air and Soil Pollution, 5(6), 533-542.
    Crossref
  15.  Lantzy.R.J and  Mackenzie.F.T, (1979), Atmospheric trace metals global cycles and assessment of man,s impact, Geochim. Cosmochim.Acta, 4(3), 511-525.
    CrossRef
  16. Houng.K.H and Lee.D.Y, (1998), Compar is one of linear and nonlinear Langmuir and Freundlich curve it in the study of Cu,VEL, and Pb adsorption on Taiwan soils, J .Soil Sci., 163 (2), 115-121.
    CrossRef
  17. Ayotte.J.D.,Nielsen.M,G.,Jr., G.R., and Moore.R.B., (1999), Relation of Arsenic, Iron and Manganese in groundwater to Aquifer Type, Bedrock Lithogeochemistry, and Land use in the New England Coastal Basins, Water Resources Investigations Report 99-4162.
  18. EPA Report, (2003), Healthy Drinking Waters for Rhode Islanders,
    EPA-39- 69.U.S.Environmental protection agency, U.S.A.
  19. Mohan. S.V, Nithila. P, and Reddy. S.J, (1996), J.Environ. Sci.Health,
    A31(2), 283.

Creative Commons License
This work is licensed under a Creative Commons Attribution 4.0 International License.

About The Author