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

Studies on Heavy Metal Contamination and Physico-chemical Properties of Godavari River Water at Rajahmundry, Andhra Pradesh

Namrata Jain and P. Srinivasa Reddy*

Department of Chemistry, Sarvepalli Radhakrishnan University, NH-12, Hoshangabad Road, Jatkhedi, Bhopal, Madhya Pradesh, India.

Corresponding Author E-mail: pothamsetty.srinivasa@gmail.com

DOI : http://dx.doi.org/10.13005/ojc/380333

Article Publishing History
Article Received on : 17 May 2022
Article Accepted on : 23 Jun 2022
Article Published : 28 Jun 2022
Article Metrics
Article Review Details
Reviewed by: Dr. Fatimah Mohamed Ali Abouzeid
Second Review by: Dr. Faiz
Final Approval by: Dr. Ioana Stanciu
ABSTRACT:

The present study is aimed to examine the water quality of the Godavari River at Rajahmundry. Water samples from Kotillingala Revu, Kovur Godavari river bridge, Saraswati Ghat, Dowleswaram, Pushkar Ghat were collected and analysed for pH, electrical conductivity, total hardness, TDS, DO, BOD, COD, nitrates. The concentration of six heavy metals were analysed quantitatively using atomic absorption spectrophotometer.

KEYWORDS:

Godavari River; Physico Chemical Parameters; Rajahmundry; Trace elements, Water Quality

Download this article as: 

Copy the following to cite this article:

Jain N, Reddy P. S. Studies on Heavy Metal Contamination and Physico-chemical Properties of Godavari River Water at Rajahmundry, Andhra Pradesh. Orient J Chem 2022;38(3).


Copy the following to cite this URL:

Jain N, Reddy P. S. Studies on Heavy Metal Contamination and Physico-chemical Properties of Godavari River Water at Rajahmundry, Andhra Pradesh. Orient J Chem 2022;38(3).Available from: https://bit.ly/3yofw00


Introduction

After Ganges, the Godavari is the longest river in India, covers total area of 312,812 km2 1, 2. It originates near Nashik, flows through five states and empties into the Bay of Bengal 3. State wise distribution of Godavari basin is represented in Fig. 1 and Fig.2.

Figure 1: State wise distribution of Godavari River.

Click here to View figure 

Figure 2: Path of the Godavari through the South Indian Peninsula.

Click here to View figure 

In Andhra Pradesh, it flows through the Papi hills 4,5. In Rajahmundry region, the river water is polluted by many industries, domestic sewage and municipal wastages. In this research work, water samples from Kotillingala Revu, Kovur Godavari river bridge, Saraswati Ghat, Dowleswaram, Pushkar Ghat in Andhra Pradesh were collected and quality of collected samples were analysed.

Materials and Methods

Study area

In Rajahmundry, the Godavari River is polluted by industrial effluents and domestic waste water 6. The name of the water quality sites, latitude and longitude are shown in Table 1. Water samples were collected once in every month from the water quality monitoring station Rajahmundry and samples were collected from the surface waters of the River. Samples were collected from June 2020 to May 2021.

Table 1:  Water quality stations on river Godavari.

Site number

Name of water quality site

Latitude and longitude

Region

S1

Kotillingala Revu

latitude —17°01’00.1″N, longitude —81°46’13.1″E

Rajahmundry

S2

Kovur Godavari river bridge

latitude —16°59′52″N , longitude —81°45′21″E

Rajahmundry

S3

Saraswati Ghat

latitude — 16°59′36.06′′N, longitude — 81°46′18.98′′E

Rajahmundry

S4

Dowleswaram

latitude – 16°57’2.51″N,

longitude – 81°46’55.18″E

Rajahmundry

S5

Pushkar Ghat

latitude —16°59’03.2″N, longitude —81°47’02.7″E

Rajahmundry

 

The analysis included 14 water quality parameters like pH, electrical conductivity, total hardness, total dissolved solids (TDS), dissolved oxygen (DO), biological oxygen demand (BOD), chemical oxygen demand (COD) and nitrates were monitored by sampling at 5 stations for 12 months (2020–2021). The quality of water samples were analysed as per the standard methods 7. Trace metal analysis was carried out using Atomic Absorption Spectrometer (AAS) following standard methods given in APHA (2012) 8.

Results and Discussion

Among the 840 observations, only maximum, minimum, mean and standard deviation values are shown in Table 2.

pH

During the study period, the water pH was slightly basic at all stations (Table 2). It ranged from 7.65 to 9.56. The mild alkaline nature of river water attributed to the presence of CO2 in water as bicarbonate 9.

Electrical conductivity

The level of salinity indicated by electrical conductivity 10. According to WHO standards, EC value within 400 μmho /cm is acceptable 11. The current investigation showed that EC value was 101 to 170 μmho/cm, which indicated the lower level of ionic concentration (Table 2).

Total dissolved solids

TDS showed a maximum value in Kotillingala Revu from September 2020 to January 2021 (410 to 441 mg/L) followed by Dowleswaram from September 2020 to December 2020 (410 to 398 mg/L). According to USPHS (United States Public Health Services, 1962) standard, TDS value should not exceed 500 mg/L 12.

DO, BOD, COD

In the present study, the range of DO over a period of one year from June 2020 to April 2021 was found to be high at all five stations, mean value in between 6.85 to 7.44 shown in Table 2. During the study period, DO content was found in between 5.12 to 8.04 at all five stations. The oxygen balance of an aquatic environment plays an important role in pollution. The B.O.D and C.O.D. are interrelated mainly due to effluents. Present study agrees with previous report, investigated by Srinivasarao et al. (2008) 13. The present study indicated that the quality of river water is in permissible limits (BIS 10500 (2012) 14 because of maximum level of DO.

Hardness

Hardness mainly due to dissolved Ca, Mg salts. In the present study, hardness found from 190 mg/l to 356 mg/l at all sites. The hard water causes kidney stones in humans 15.

Nitrate

Concentration of nitrates was highest in Dowleswaram , January 2021 (18 mg/L) followed by Kotillingala Revu, January 2021 (16.3 mg/L) and least in Pushkar ghat , June 2020 (3.8 mg/L). Because of flood, nitrates contributing algae from rocks minimizes fixation of nitrates during June to September 2020 in all stations.

Table 2: Maximum, minimum, mean and SD values of water quality parameters.

Parameters

 

S1

S2

S3

S4

S5

pH

Max

9.56

8.95

9.05

9.56

8.90

Min

7.98

7.89

7.99

7.86

7.65

Mean

8.30

8.29

8.64

8.41

8.26

SD

0.3980

0.3157

 0.3499

0.4755

0.2943

Electrical conductivity

Max

145

140

167

170

138

Min

117

101

104

110

111

Mean

130

121

121

139

126

SD

9.5956

11.0138

15.8508

16.5300

8.0501

Total hardness

Max

325

300

290

356

290

Min

200

200

190

280

210

Mean

287

254

234

291

258

SD

34.8937

35.3886

32.7781

35.7149

23.7679

TDS

Max

442

392

376

410

389

Min

257

198

221

320

259

Mean

359

294

296

353

320

SD

56.7058

46.8549

48.8532

30.2851

44.2576

DO

Max

7.98

7.80

8.04

7.90

7.45

Min

5.12

6.06

7.08

6.24

5.86

Mean

7.08

7.03

7.44

7.15

6.85

SD

0.8033

0.4851

0.3387

0.4012

0.6381

BOD

Max

20.2

19.2

17.8

15.2

16.7

Min

10.8

12.2

12.2

10.5

10.9

Mean

15.7

14.8

14.0

12.8

13.6

SD

3.1808

2.0218

1.5564

1.1033

1.6140

COD

Max

110.2

110.8

110.2

113.1

114.3

Min

69.8

69.6

71.2

70.8

77.8

Mean

92.4

91.7

94.6

95.5

93.1

SD

13.1239

14.5871

12.2742

12.9126

13.2803

Nitrates

Max

16.3

8.9

8.0

18.0

11.0

Min

6.7

3.0

3.8

6.2

3.8

Mean

10.7

4.8

5.0

11.3

6.20

SD

3.0153

1.7281

1.2697

4.1574

 2.0320

Chromium (µg/L)

Max

14.45

13.50

3.72

6.90

7.92

Min

2.28

4.50

0.34

1.28

1.17

Mean

8.14

9.44

1.96

4.38

4.14

SD

3.3730

2.6448

1.0332

2.0431

2.4005

Copper (µg/L)

Max

18.12

28.08

3.08

6.28

8.88

Min

6.20

1.40

0.20

0.20

0.18

Mean

11.95

6.29

1.36

2.59

3.46

SD

3.9826

7.0143

0.9014

1.8980

2.3940

Nickel (µg/L)

Max

17.08

19.28

11.28

12.38

11.20

Min

4.10

3.45

1.56

1.30

1.10

Mean

10.23

10.42

5.81

6.92

4.42

SD

4.1921

4.1547

2.9878

3.0293

 2.8891

Lead (µg/L)

Max

4.50

5.05

3.40

3.90

3.56

Min

1.23

1.20

0.45

0.78

0.77

Mean

2.77

3.19

1.47

2.21

1.92

SD

0.9547

1.1690

0.9062

0.9861

0.8229

Zinc (mg/L)

Max

0.112

0.108

0.1

0.1

0.1

Min

0.008

0.0008

0.003

0.008

0.0006

Mean

0.089

0.0372

0.0789

0.067

0.0638

SD

0.0251

0.0444

0.0306

0.0366

0.0443

Iron (mg/L)

Max

0.180

0.04

0.04

0.190

0.04

Min

0.01

0.008

0.008

0.01

0.003

Mean

0.0825

0.0917

0.01725

0.06083

0.01925

SD

0.0521

 0.0110

0.0085

0.0608

0.0123

 

Chromium

Chromium is used in many industries [16]. These industries discharge Cr (III) and Cr (VI).  Cr (VI) is carcinogenic and toxic 17. From the Table 2, chromium concentration found from 0.34 to 14.45 µg/L (within acceptable limit 50 µg/l). The maximum chromium concentration (14.45 µg/L) was found at Kotillingala Revu in April 2021.

Copper

The intake of large amount of copper causes chronic health issues 18.  From the present investigation, copper concentration was found between 0.18 and 28.08 µg/L, within the acceptable limit of 50 µg/l 14. The highest copper concentration (28.08 µg/L) was observed at Kovur in May 2021 and minimum copper concentration (0.18 µg/L) was found at Pushkar ghat in June 2020.

Nickel

Nickel concentration found in between 1.10 to 19.28 µg/L. The maximum nickel concentration (19.28 µg/L) was found at Kovur Godavari river bridge in April 2021.

Lead

Intake of excess of lead causes adverse health effects, severely affect the CNS, loss of memory. In adults, chronic lead toxicity leads to joint pain and gastrointestinal symptoms19. Lead concentration varies from o.45 to5.05 µg/L, but within the acceptable limit of 10µg/L. The maximum lead concentration (5.05 µg/L) was found in Kovur Godavari river bridge at April 2021.

Zinc

Zinc concentration found from 0.0006 to 0.112 mg/L (acceptable limit 5 mg/L). The maximum lead concentration (0.112 mg/L) was found in Kotillingala Revu in May 2021.

Iron

The intake of large amount of iron leads tissue damage [18]. Iron concentration found in between 0.003 to 0.190 mg/L, however within the acceptable limit of 0.3 mg/L. The maximum iron concentration (0.190 mg/L) was found in Dowleswaram in January 2021.

According to BIS 10500 (2012), the requirement (acceptable limit) is given in Table 3.

Table 3:  Drinking water standards for trace elements (BIS-10500-2012).

Trace elements

Acceptable limit

Chromium

 50 µg/L

Copper

 50 µg/L

Nickel

 20 µg/L

Lead

 10 µg/L

Zinc

 5 mg/L

Iron

 0.3 mg/L

 

In this study,  various physico-chemicals parameters were recorded throughout the year. The results showed that, these parameters are seasonally varied and are found to depend on environmental and other factors. Most of the parameters are within acceptable range compared to given by USPHS (1962) and BIS 10500 (2012) standards. The results presented in this study are consistent with the previous observations 20,21. The pH, temperature, and the water disturbance affect the levels of these heavy metals in an aquatic environment. For example, heavy metals are released more easily into the water at lower pH and higher temperatures. Although many metals are considered essential, they become toxic at higher concentrations due to their ability to cause oxidative stress by forming free radicals, which can react with cellular structure proteins, enzymes and membrane systems 22. The pollution of heavy metals in our atmosphere, soils and waters are all due to human activity 23. Heavy metals can be removed from water. Agricultural waste, such as dairy manure, remaining waste material from rice and peanuts, natural soil seem to be the best to remove heavy metals24.

Conclusion

Based on findings, it was concluded that the water from the study area is basic in nature and saturated with dissolved oxygen. Godavari river is being polluted with the discharge of industrial effluents at Rajahmundry. There is an urgency to take up protection of river water.

Acknowledgement

Authors sincerely thanks to Shanmuga Centre for Medicinal Plants Research, Thanjavur, Tamil Nadu, India for water quality studies.

Conflicts of Interests

The authors declare no conflict of interest.

Funding Sources

There is no funding sources

References

  1. The Godavari River System. cwc.gov.in. Central Water Commission, Ministry of Jal Shakti, Department of Water Resources, River Development and Ganga Rejuvenation.
  2. Babar M, Kaplay RD (2018) Godavari River: Geomorphology and Socio-economic Characteristics. In: Singh D. (eds) The Indian Rivers. Springer Hydrogeology. Springer, Singapore. https://doi.org/10.1007/978-981-10-2984-4_26.
  3. Integrated Hydrological DataBook (Non-Classified River Basins). Central Water Commission. p. 9.
  4. Polavaram project studies by NGT (page 56). http://www.indiaenvironmentportal.org.in/files/file/Polavaram-project-report-NGT.pdf
  5. Amarnath C R, Thatikonda S. Water, 2020; 12:576. doi:10.3390/w12020576.
  6. Akkaraboyina MK, Raju BSN. Universal J. Environ. Res. Tech., 2012;2(2):161-167.
  7. American Public Health Association (APHA), 2005. Standard Methods for the Examination of Water and Wastewater. 21st edn., American Public Health Association, Washington, DC. 2-61.
  8. American Public Health Association (APHA), 2012. Standard methods for the examination of water and wastewater, 22nd edn. Edited by Rice EW, Baird RB, Eaton AD, Clesceri LS. American Public Health Association, Washington, D.C., USA.
  9. Azeez PA, Nadarajan NR, Mittal DD. Pollut. Res., 2000;19(2):249-255.
  10. Rusydi AF. IOP Conf. Series: Earth Environ. Sci., 2018;118: 012019. doi :10.1088/1755-1315/118/1/012019.
  11. Meride Y, Ayenew B. Environ. Syst. Res., 2016;5. DOI 10.1186/s40068-016-0053-6.
  12. Bhalla R, Waykar BB. Nat. Environ. Pollut. Technol., 2013;12(1):125 -129.
  13. Srinivasarao V, Khan AM. J. Ind. Pollut. Control., 2008;24(1):1-8.
  14. Bureau of Indian Standards (BIS) 10500 (2012) Specification for drinking water. Indian Standards Institution, New Delhi, pp 1–5.
  15. Rai AK, Paul B, Mudra L, Kishor N. J. Adv. Lab. Res. Biol., 2011;2(4):136-140.
  16. Ganguli A, Tripathi AK. Appl. Microbiol. Biotechnol ., 2002;58:416–420.
  17. Lee SE, Lee JU, Chon HT, Lee JS. Microbiological reduction of hexavalent chromium by indigenous chromium-resistant bacteria in sand column experiments. Environ. Geochem. Health., 2008;30:141–145.
  18. Hussain J, Husain I, Arif M. Environ. Quality., 2014;14:31-41.
  19. Ogwuegbu MOC, Muhanga. W. J. Environ, 2005;1:66–75.
  20. Hussain J, Husain I, Arif M, Gupta N. Appl. Water Sci., 2017;7:4539–4548.
  21. Samanta S, Kumar V, Nag SK, Saha K, Sajina AM, Bhowmick S, Paul SK, Das BK. Aquat. Ecosys. Health Manag., 2021;24 (4):23–33.
  22. Apau J, Osei-Owusu J, Yeboah A, Gyamfi O, Darko G, Akoto O, Dodd M, Sci. Afr., 2022;15:e01074.
  23. Briffa J, Sinagra E, Blundell R. Heliyon, 2020;6(9);e04691.
  24. Joseph L,  Jun BM,  Flora JRV,  Park CM,  Yoon Y. Chemosphere, 2019;229:142-159.

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

About The Author