Submit manuscript...
International Journal of
eISSN: 2576-4454

Hydrology

Research Article Volume 5 Issue 2

Status of heavy metals contamination in drinking water of district D. G. Khan, Punjab, Pakistan

Farhad Ahmad,1 Aniqa Batool,1 Muhammad Asad Ghufran,2 Syeda Sabahat Kazmi3

1Department of Environmental Sciences, Pir Mehr Ali Shah-Arid Agriculture University Rawalpindi, Pakistan
2Department of Environmental Science, International Islamic University Islamabad, Pakistan
3National Physical and Standardization Laboratories, Pakistan

Correspondence: Aniqa Batool, Lecturer, Department of Environmental Sciences, Pir Mehr Ali Shah-Arid Agriculture University Rawalpindi, Shamsabad Murree Road Rawalpindi 46300, Pakistan

Received: February 04, 2021 | Published: March 30, 2021

Citation: Ahmad F, Batool A, Ghufran MA, et al. Status of heavy metals contamination in drinking water of district D. G. Khan, Punjab, Pakistan. Int J Hydro. 2021;5(2):39-44. DOI: 10.15406/ijh.2021.05.00264

Download PDF

Abstract

Anthropogenic activities are the major cause of environmental pollution. Industrialization, urbanization and agriculture activities are also causing huge troubles linked to human health in Pakistan. Heavy metals contamination has increased in drinking water because of urbanization and agricultural activities. Being one of the urbanized Cities, Dera Ghazi Khan has also been subjected to the hastily increasing harms of contamination. The respective study was planned to evaluate the heavy metals concentrations and identification of high risk areas for the inhabitants living in the city. Total ninety-six samples of drinking water were collected. TDS and EC were in the range of 1.48 to 8.412 mg/L and1.41 to 9.4µS/cm respectively. TSS was from 40 to 599 mg/L which were exceeding WHO guidelines in eight samples. Heavy metals such as Ni, Cr, Zn, Pb and Cd were measured through atomic absorption spectrophotometer. Zn average value was well within WHO standard while Pb was exceeded in thirty-nine samples. Cd was exceeded in fifteen samples; Cr and Ni were exceeded in eighteen samples. Sources of heavy metals identified as agricultural activities, domestic and commercial effluent. Ground water samples were found potable at some locations but at the same time pose serious threat to human health due to heavy metals above permissible limits.

Keywords: drinking water, heavy metals, environmental, pollution, dera ghazi khan

Introduction

Water is a universal solvent, having ability to dissolve lethal organic and inorganic compounds which are not only deteriorating the water’s worth but also effects consumer’s fitness.1 The total percentage of fresh water on the earth is 3-4% while 0.01% is used for human needs.2 In developing countries, more than 80% population use ground water for drinking purposes.3 The heavy use of fresh water in industry, agriculture and municipal facilities is causing contamination in fresh water while the demand of uncontaminated water is rapidly increasing in most polluted regions.5 Presence of some trace elements is reported to be necessary for human health in drinking water but the elevated concentration or the accumulation of these trace metals may cause harmful effects.5

Inorganic pollutants occur naturally or industrial influences or watershed from farming include many heavy metals like Zn, Cu, Cr, Mn and Ni.6 The elements which have more than 6 g/cm3 atomic density are known as heavy metals and most persistent pollutants in water.7 The certain absorption of heavy metals become toxic when they exceed from permissible limit8 while heavy metals are disseminated in all mediums of nature such as water, air and soil. Some heavy metals are present at low concentration in every medium of nature and they can carry about massive destruction to the environment when their consumption exceeds from the safe limit.9

In Pakistan, drinking water quality and its progresses is an important problem and about 44% of total population has no access to harmless drinking water.10 Drinking water must be secured from illness producing agents before human consumption.11 Surface and ground water sources in Pakistan contaminated and international standards for chemical limits for drinking water cannot follow.12 Two other factors Koh-e-Suleman in the west of city and Indus river in the east are also responsible for changing chemical behavior of ground water to make it unfit for human consumption.13 The demand of pure drinking water has increased with this tremendous increase in population. The purpose of the study was to evaluate the drinking water quality available for the population of Dera Ghazi Khan City, built on a set of precise parameters. The main objectives of the study were following:

  1. Determination of concentration of heavy metals such as Pb, Ni, Cr, Cd and Zn in drinking water of D. G. Khan city
  2. Determination of variation in chemical composition of drinking water from block to block and block to source and identification of high risk areas for the inhabitants living in the city of D. G. Khan.

Materials and methods

Study area

D. G. Khan (Lat: 30º; Lon: 70º), is the district of Punjab province (Pakistan) was selected as study area to assess heavy metals contamination in drinking water. The average annual rainfall of Dera Ghazi Khan is 155 mm. Temperature of the D. G. Khan city during summer season usually about 46 ºC and during winter season becomes very low reaching 4 ºC.

Sample collection

The samples were collected from 32 different locations of D. G. Khan city from hand pumps with different depth ranging from 10 to 50 m which were used for drinking purpose (Figure 1). Total ninety-six samples were collected. Samples were collected in polyethylene bottles (PET) with 1 liter capacity. Before filling the sample bottles were rinsed by distilled water. For physico-chemical parameters, the samples were preserved in ice box at 4 ºC before the analyses.

Figure 1 Map (From Google Map) of Dera Ghazi Khan showing sampling sites of the study area.

Analytical methods

Temperature measurement was done on the sampling site through using the mercury filled Celsius thermometer. Multimeter Crison (MM40+) was used to check the pH (APHA, 2005). By using multimeter Crison (MM40+), electrical conductivity was measured of all the obtained samples in the laboratory (APHA, 2005). Furthermore, using same multimeter Crison (MM40+) the concentration of total dissolved solids were also estimated. While total suspended solids were measured by using micro filters and drying the residues at 103-105 ºC as per following standard methods (APHA, 2005).

Heavy metals

Lead, chromium, cadmium, zinc and nickel concentration in water samples were determined through atomic absorption spectrophotometer (AAS) (GBC 932+ following APHA (2005). The detection wave lengths for Pb, Cr, Cd, Zn and Ni were 217 nm, 357.9 nm, 228.8 nm, 213.9 nm, 232 nm, respectively.

Statistical analysis

Descriptive statistics was applied for the data analyses while t-test was performed in order to compare the results of the study with WHO and GoP guidelines value. Furthermore MS Excel and Statistix (ver. 8.1) softwares were used to manipulate data.

Results

The Consumption of heavy metals through water and food chain is a major threat to human and its environment. Heavy metals contamination is prominent in increasing its destructive impacts. So, the quality of drinking water was tested by obtaining samples from thirty two different locations in the D. G. Khan City and six significant drinking water quality parameters (temperature, pH, EC, TDS, TSS and five heavy metals) in obtained ninety-six samples were investigated.

Temperature

Temperature measurements of the collected samples from all thirty-two sampling site ranged from 20.5 to 28.3 C. Lowest temperature was measured at sampling site of Block K within average temperature of 20.5 C and highest temperature within average temperature of 28.3 C was observed at location ‘Pul Daat’.

pH

The pH concentration of the obtained samples from all the thirty-two locations was found in the range of 6.98 to 8.17. Among all the sampling sites, in sampling location block 42 lowest pH value was determined (6.98), while in sampling site of ‘Chouratha’ highest pH value was found (8.17).

Electrical conductivity (EC)

The EC measurements ranged from 1.41 to 9.4µS/cm. The lowest EC concentration was measured in ‘Mastoi Abad’ within average concentration of 1.41µS/cm and at location Block D, highest mean concentration was measured within 9.4µS/cm among all sampling site.

Total dissolved solids (TDS)

The mean concentration of TDS ranged from 1.480 to 8.412 mg/L from the entire sampling site. The lowest TDS value was also observed in ‘Mastoi Abad’ with mean concentration of 1.41 mg/L and highest average concentration was observed at Block D within 8.412 mg/L.

Total suspended solids (TSS)

The TSS concentration measured for all the ninety-six samples from all the locations of D. G. Khan ranged from 40 to 599 mg/L among all the samples. Highest concentration was found at ‘Abbas Abad’, ‘Allah Abad’ and ‘Chouratha’ with the mean concentration of 599 mg/L, 590 mg/L and 573 mg/L respectively.

Heavy metals

Concentrations of five heavy metals in all the ninety-six samples collected from different thirty-two location of Dera Ghazi Khan City were investigated.

Zinc

Zinc was not detected in the samples of two locations. The values of Zn in all the samples of D. G. Khan were less than 3 mg/L. Average concentration of Zn was observed ranging from 0.229 to 2.524 mg/L. Zinc concentration in all the samples was below the WHO guidelines limits (Figure 2).

Figure 2 Mean values of Zinc observed in collected drinking water samples.

Chromium

The chromium concentration was found at nine locations of different sampling site of the D. G. Khan city. The average concentration of Cr ranged from 0.035 to 0.049 mg/L among all the samples which was below the WHO guidelines level (Figure 3). Overall mean concentration of chromium of D. G. Khan in drinking water was 0.0043 mg/L. The lowest concentration was observed at ‘Abbas Abad’ with the average concentration of 0.035 mg/L but highest concentration was observed at Block 28 and ‘Chouratha’ with same mean concentration of 0.049 mg/L.

Figure 3 Mean values of Chromium observed in collected drinking water sample.

Nickel

Nickel Concentration was detected from seven different locations of the city in twenty-one samples of water. The mean concentration of Ni ranged from 0.027 to 0.051 mg/L among all the samples. Highest concentration was observed at ‘Umer Town’ with the mean concentration of 0.051 mg/L. Overall average concentration of Ni was found to be 0.042 mg/L in the samples (Figure 4).

Cadmium

Figure 4 Mean values of Nickel observed in collected drinking water samples.

Cadmium concentration was observed highest at sampling site of ‘Chouratha’ with the average concentration of 0.005 mg/L. Overall mean concentration was observed 0.0038 mg/L among all the samples (Figure 5).

Figure 5 Mean values of Cadmium observed collected drinking water samples.

Lead

Lead concentration was observed highest at sampling location ‘Chouratha’ with the mean concentration of 0.049 mg/L while it was observed lowest at sampling location Block 16 with the mean concentration of 0.007 mg/L (Figure 6).

Figure 6 Mean values lead observed in collected drinking water samples.

Discussion

Physico-chemical parameters like temperature, pH, EC, TDS and TSS results showed a considerable relation among all the samples. Odorless results obtained in drinking water of D. G. Khan city among all the samples which were within WHO guidelines and showing well aesthetic qualities. pH of water is considered as the most significant parameter for testing water quality which shows the acid base stability and is used as a tool for analyzing the water chemistry.14 pH in most of the samples of study area showed significant relation with the low concentration of heavy metals. Electrical conductivity (EC) was measured in the range of 1.41 to 9.4µS/cm, which was high in all the samples of water. The areas which are near to the mountains of ‘Fort Munro’ in the west may be the possible reason for high values of EC due to their geographical location. Increase rate of ions in water is directly linked to electrical conductivity because of mineral weathering, nitrate and sulphate concentrations. Total dissolved solids concentrations were exceeding from WHO limits. It was observed that average values of TDS and EC give coincidence relationship between two values from all location in this study. The concentration of suspended particles and values of metals have a strong correlation.15 According to the U.S. EPA (2000), total suspended solids are formed on the basis of mineral content in water. The concentration of TSS in drinking water of D. G. Khan was found in satisfactory condition in eighty-eight samples i.e. within WHO limits.

In the current assessment, the drinking water samples were observed to have the cadmium concentration in the range of 0.0026 to 0.005 mg/L. The high concentration of Cadmium was measured in eighteen samples in those areas which are located in the west near mountains of Koh-e-Suleman and vehicular activities are more than other areas. The lowest concentration was observed at ‘Abbas Abad’ with the average concentration of 0.035 mg/L but highest concentration was observed at Block 28 and Chouratha with same mean concentration of 0.049 mg/L. Dissolution of chromium from rock strata may be considered as source in drinking water of D. G, Khan because of Fort Munro Hills in the west. In the obtained samples from different locations, lead average concentration was observed in the range of 0.007 to 0.049 mg/L. Agricultural activities can be considered as the major source of Zn contamination in drinking water of city. The mean concentration of Ni ranged from 0.027 to 0.051 mg/L among all the samples except one sampling site (Block 48). Highest concentration was observed at ‘Umer Town’ with the mean concentration of 0.051 mg/L. Leaching from mining, industrial activities and weathering from different types of rocks can be considered as the sources of Ni contamination in drinking water.16 So the waste material from cement factory and Ghazi tractor factory may be the source of Ni contamination in city. Heavy population, commercial and domestic effluent and agricultural activities are responsible of variation among heavy metals in drinking water. On current data basis, following recommendations are made:

  1. Water treatment plants should be installed at different locations of city to ensure the access of clean drinking water. So that heavy metals contamination could be checked.
  2. A centralized sewerage system should be developed in D. G. Khan city as well as its marginal regions to evade domestic waste percolation seeping in to the aquifer.
  3. Regular monitoring of all water resources and water points should be ensured to help determine problem regions, source of pollution and design a frame work of corrective plans.17–33

Acknowledgments

None.

Conflicts of interest

The author declares there is no conflict of interest.

References

  1. Beamonte E, JD Bermudez, A Casino, et al. A statistical study of the quality of surface water intended for human consumption near Valencia (Spain). J Env Manage. 2007;83:307–314.
  2. Hinrichsen D, H Tacio. The coming freshwater crisis is already here. The linkages between population and water. Washington, DC: Woodrow Wilson Internat. Cent Scho. 2002. p. 1–26.
  3. Pedley S, G Howard. The public health implications of microbiological contamination of groundwater. The Quarter. J Eng Geology. 1997;30:179–188.
  4. Zahoorullah T, Akhtar, S Zai. Quality of drinking water in rural Peshawar. Pak J Med Res. 2003;42(3):85–89.
  5. Mastoi GM, SGS Shah, MY Khuhawar. Assessment of water quality of Manchar Lake in Sindh (Pakistan). Environ. Monit Assess. 2008;141:287–296.
  6. Paustenbach DJ, BL Finley, FS Mowat, et al. Human health risk and exposure assessment of chromium (VI) in tap water. J Toxicol Environ Health A. 2003;66(14):1295–1339.
  7. Akpor OB, M Muchie. Remediation of heavy metals in drinking water and wastewater treatment systems: Processes and applications. Int J Physic Sci. 2010;5(12):1807–1817.
  8. Babich H, G Stotzky. Environmental factors that influence the toxicity of heavy metals and gaseous pollutants to microorganisms. CRC Critical Reviews in Microbiology. 1980;8:99–145.
  9. Kenish MJ. Ecology of Estuaries: Anthropogenic Effects. CRC Press, Inc., Boca Raton, FL, 1992. p. 494.
  10. Farooq S, I Hashmi, IA Qazi, et al. Monitoring of Coliforms and chlorine residual in water distribution network of Rawalpindi, Pakistan. Environ Monit Asses. 2008;140:339–347.
  11. Guideline for Drinking Water Quality. 3rd edn, (Electronic Source). 2006.
  12. Javaid S, SGS Shah, AJ Chaudhary, et al. Assessment of trace metal contamination of drinking water in the pearl valley Azad Jammu and Kashmir. Clean Soil Air Water. 2008;36(2):216–221.
  13. Malana MA, MA Khosa. Groundwater pollution with special focus on arsenic, Dera Ghazi Khan, Pakistan. J Saud Chem Soc. 2011;15(1):39–47.
  14. Baig JA, TG Kazi, MB Arain, et al. Evaluation of arsenic and other physico-chemical parameters of and ground water of Jamshoro. Pak J Hazard Matter. 2009;166(2–3):662–669.
  15. Lawson NM, PR Mason. Concentration of mercury, methyl mercury, cadmium, lead, arsenic and selenium in the rain and stream water of two contrasting watershed in Western Maryland. Water Research. 2001;35(17):4039–4052.
  16. Khan S, IA Shah, S Muhammad, et al. Arsenic and heavy metal concentrations in drinking water in Pakistan and risk assessment: a case study. Human and ecological Risk assessment International Journal. 2015;21:1020–1031.
  17. Das S, SC Patnaik, HK Sahu, et al. Heavy metal contamination, physico-chemical and microbial evaluation of water samples collected from chromite mine environment of Sukinda, india. Trnsac Nonferrous Metal Society. 2013;23:484–493.
  18. Farooqi A, H Masud, M Kusakabe, et al. Distribution of highly arsenic and fluoride contaminated groundwater from east Punjab, Pakistan, and the controlling role of anthropogenic pollutants in the natural hydrological cycle. Geochem J. 2007;41:213–234.
  19. Howard G, S Pedley, M Barret, et al. Risk factors contributing to microbiological contamination of shallow ground water in Kampala Uganda. Water Res. 2003;37(14):3421–3429.
  20. Hurst CJ. Estimating the risk of acquiring infectious disease from ingestion of water. Chapter 4. In: C. J. Hurst (ed.), Modeling Disease Transmission and its Prevention by Disinfection. Cambridge University Press, Cambridge. 1996. p. 99–139.
  21. Muhammad S, MT Shah, S Khan. Arsenic health risk assessment in drinking water and source appointment using multivariate statistical technique in Kohistan region, Northern Pakistan. Food Chem Toxicol. 2010;48:2855–2864.
  22. Muhammad S, MT Shah, S Khan. Health risk assessment of heavy metals and their source apportionment in drinking water of Kohistan region, northern Pakistan. Microchem J. 2011;98:334–343.
  23. Peter NE. Evaluation of environmental factors affecting yields of major dissolved ions of streams in the United States. USGS water-supply. 1984. p. 2228.
  24. Sajil Kumar PJ, PD Delson, PT Babu. Appraisal of heavy metal in groundwater in Chennai city using a HPI model. Bull Environ Cont Toxicol. 2012;89:793–798.
  25. Santos AE, Alonso M, Callejo’n, et al. Heavy metal content and speciation in ground water of the Guadiamar river basin. Chemosphere. 2002;48:279–285.
  26. Shi G, Z Chen, S Xu, et al. Potentially toxic metal contamination of urban soils and roadside dust in Shanghai, China. Environ Pollution. 2008;156:251–260.
  27. Wang H, CX Wang, ZJ Wang, et al. Fractionation of heavy metals in surface sediments of Taihu lake, China. Environ. Geochem Health. 2004;26(2):303–309.
  28. Wang M, Y Xu, S Pan. Long-term heavy metal pollution and mortality in a Chinese population: an ecologic study. Biol Trace Elem Res. 2010;142(3):362–379.
  29. Guidelines for drinking water quality. Geneva: World Health Organization. 2003. p. 81–87.
  30. Woo NC, MJ Choi, KS Lee. Assessment of ground water quality and contamination from Uranium bearing balck shale in Goesan-Boeun areas, Korea. Environ Geochem Health. 2002;24(3):264–273.
  31. Woo NC, MJ Choi, KS Lee. Assessment of groundwater quality and contamination from Uranium-Bearing Shale in Goesan-Boeun areas, Korea. Environ Geochem Health. 2002;24(3):264–274.
  32. Wyatt CJ, C Fimbres, L Romo, et al. Incidence of heavy metal contamination in water supplies in Northern Mexico. Environ Res 1998;76:114–119.
  33. Zacheus OM, PJ Martikainen. Physicochemical quality of drinking and hot waters in finish buildings originated from ground water or surface water plants. Sci Total Environ. 1997;204:1–10.
Creative Commons Attribution License

©2021 Ahmad, et al. This is an open access article distributed under the terms of the, which permits unrestricted use, distribution, and build upon your work non-commercially.