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www.theijoem.com Vol 4 Number 2; April, 2013 80 This work is licensed under a Creative Commons Attribution- NonCommercial 3.0 Unported License. To review this article online, scan this QR code with your Smartphone Original Article Concentrations of Mercury, Lead, Chromium, Cadmium, Arsenic and Aluminum in Irrigation Water Wells and Wastewaters Used for Agriculture in Mashhad, Northeastern Iran SR Mousavi 1 , M Balali-Mood 1 , B Riahi-Zanjani 1 , H Yousefzadeh 2 , M Sadeghi 1 1 Medical Toxicol- ogy Research Center,Department of Clinical toxicology, School of Medicine, Mashhad University of Medical Sciences, Mashhad, Iran 2 Department of Cel- lular and Molecular Immunology, Mashhad University of Medical Sciences, Mashhad, Iran Correspondence to Mahmood Sadeghi, MSc, Medical Toxicol- ogy Research Center, Department of Clinical toxicology, School of Medicine, Mashhad University of Medical Sciences, Mashhad, Iran Tel: +98-511-800-2464 Fax: +98-511-800-2467 E-mail: sadeghi. [email protected] Received: Nov 5, 2012 Accepted: Jan 20, 2013 Abstract Background: Contamination of water by toxic chemicals has become commonly recognized as an environmental concern. Based on our clinical observation in Mashhad, northeastern Iran, many people might be at risk of exposure to high concentrations of toxic heavy metals in water. Because wastewater effluents as well as water wells have been commonly used for irrigation over the past decades, there has been some concern on the toxic metal exposure of crops and vegetables irrigated with the contaminated water. Objective: To measure the concentrations of mercury, lead, chromium, cadmium, arsenic and aluminium in irrigation water wells and wastewaters used for agriculture in Mashhad, northeastern Iran. Methods: 36 samples were taken from irrigation water wells and a wastewater refinery in North of Mashhad at four times—May 2008, March 2009, and June and July 2010. Atomic absorption spectrometry was used to measure the concentration of toxic metals. Graphite furnace was used for the measurement of lead, chromium, cadmium and aluminum. Mercury and arsenic concentrations were measured by mercury/hydride system. Results: Chromium, cadmium, lead and arsenic concentrations in the samples were within the standard range. The mean±SD concentration of mercury in irrigation wells (1.02±0.40 µg/L) exceeded the FAO maximum permissible levels. The aluminum concentration in ir- rigation water varied significantly from month to month (p=0.03). All wastewater samples contained high mercury concentrations (6.64±2.53 µg/L). Conclusion: For high mercury and aluminum concentrations, the water sources studied should not be used for agricultural use. Regular monitoring of the level of heavy metals in water and employing the necessary environmental interventions in this area are strongly recommended. Keywords: Food contamination; Agriculture; Sewage; Spectrophotometry, atomic; Met- als, heavy; Water pollution, chemical; Water wells; Waste water; Iran Cite this article as: Mousavi SR, Balali-Mood M, Riahi-Zanjani B, et al. Concentrations of mercury, lead, chromium, cadmium, arsenic and aluminum in irrigation water wells and wastewaters used for agriculture in Mashhad, northeastern Iran. Int J Occup Environ Med 2013;4:80-86.

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Original Article

Concentrations of Mercury, Lead, Chromium, Cadmium, Arsenic and Aluminum in Irrigation Water Wells and Wastewaters Used for Agriculture in Mashhad, Northeastern IranSR Mousavi1, M Balali-Mood1, B Riahi-Zanjani1, H Yousefzadeh2, M Sadeghi1

1Medical Toxicol-ogy Research Center,Department of Clinical toxicology, School of Medicine, Mashhad University of Medical Sciences, Mashhad, Iran2Department of Cel-lular and Molecular Immunology, Mashhad University of Medical Sciences, Mashhad, Iran

Correspondence to Mahmood Sadeghi, MSc, Medical Toxicol-ogy Research Center, Department of Clinical toxicology, School of Medicine, Mashhad University of Medical Sciences, Mashhad, IranTel: +98-511-800-2464Fax: +98-511-800-2467E-mail: [email protected]: Nov 5, 2012Accepted: Jan 20, 2013

Abstract

Background: Contamination of water by toxic chemicals has become commonly recognized as an environmental concern. Based on our clinical observation in Mashhad, northeastern Iran, many people might be at risk of exposure to high concentrations of toxic heavy metals in water. Because wastewater effluents as well as water wells have been commonly used for irrigation over the past decades, there has been some concern on the toxic metal exposure of crops and vegetables irrigated with the contaminated water.

Objective: To measure the concentrations of mercury, lead, chromium, cadmium, arsenic and aluminium in irrigation water wells and wastewaters used for agriculture in Mashhad, northeastern Iran.

Methods: 36 samples were taken from irrigation water wells and a wastewater refinery in North of Mashhad at four times—May 2008, March 2009, and June and July 2010. Atomic absorption spectrometry was used to measure the concentration of toxic metals. Graphite furnace was used for the measurement of lead, chromium, cadmium and aluminum. Mercury and arsenic concentrations were measured by mercury/hydride system.

Results: Chromium, cadmium, lead and arsenic concentrations in the samples were within the standard range. The mean±SD concentration of mercury in irrigation wells (1.02±0.40 µg/L) exceeded the FAO maximum permissible levels. The aluminum concentration in ir-rigation water varied significantly from month to month (p=0.03). All wastewater samples contained high mercury concentrations (6.64±2.53 µg/L).

Conclusion: For high mercury and aluminum concentrations, the water sources studied should not be used for agricultural use. Regular monitoring of the level of heavy metals in water and employing the necessary environmental interventions in this area are strongly recommended.

Keywords: Food contamination; Agriculture; Sewage; Spectrophotometry, atomic; Met-als, heavy; Water pollution, chemical; Water wells; Waste water; Iran

Cite this article as: Mousavi SR, Balali-Mood M, Riahi-Zanjani B, et al. Concentrations of mercury, lead, chromium, cadmium, arsenic and aluminum in irrigation water wells and wastewaters used for agriculture in Mashhad, northeastern Iran. Int J Occup Environ Med 2013;4:80-86.

www.theijoem.com Vol 4 Number 2; April, 2013 81

Introduction

Agricultural, industrial and anthro-pogenic wastes may contaminate irrigation water wells and waste-

waters with toxic heavy metals.1-3 Man-dour and Azab reported aluminum, cad-mium, nickel and lead contamination in surface drinking water of Dakahlia Gov-ernorate, Egypt.4,5 There is an increasing awareness of the hazards posed by envi-ronmental contamination with toxic ele-ments.6 Many studies have so far been published on heavy metal contamination because of their effects on human health and ecosystem.7-9 The use of industrial or municipal wastewater for irrigation in ag-riculture is common in many parts of the world; this has created opportunities and problems.10-12 The advantages of waste-water irrigation are to disposal of wastes and preparing valuable plant nutrients.13 However, it seems that heavy metal con-tent of soil is increased by wastewater irrigation.12-14 Several studies from de-veloping countries reported toxic metal contamination in wastewaters.14-17

Heavy metals such as lead, mercury, cadmium, chromium, arsenic and alu-minum have harmful effects on human health. The health effects of human ex-posure to these environmental pollutants are well documented. Some of these are nervous system and brain damage, kidney dysfunction and cancer.18

So far, many analytical techniques have been proposed for the measure-ment of concentrations of heavy met-als in water samples; those include spectrophotometry,19 ion chromatog-raphy,20 atomic absorption spectrome-try,21,22 inductively coupled plasma atomic emission spectrometry (ICP-AES)23,24 and near-infrared spectroscopy25.

Industrial and home wastewater efflu-ents as well as irrigation water wells have been commonly used for irrigation of ag-

ricultural lands for decades. For the con-cerns on the safety of crops and vegetables irrigated with contaminated water and re-fined wastewater, we therefore, conduct-ed this study in an area near Mashhad, northeastern Iran, to measure the levels of mercury, lead, chromium, cadmium, arsenic and aluminum in irrigation wa-ter wells and wastewater stations, which were used for irrigation of the surround-ing agricultural lands.

Materials and Methods

This study was carried out in an area near Mashhad city, the so-called Dashte Mash-had, where is close to an industrial town (Toos) and a wastewater refinery (Par-kand-Abad). Dashte Mashhad is almost 3351 km2 wide and located in the North-east of Iran. Figure 1 shows the study area, as well as the positions of the industrial town and wastewater refinery.

Wastewaters are one of the sources for irrigation in Dashte Mashhad. There are plants of fluorescent lamps, batteries and similar chemical industries in Toos indus-trial town which is located closely above the level of agricultural water wells. Their wastes contain mercury, lead and prob-ably other heavy metals. Since there was no appropriate wastewater system for the industrial town, it was very likely that wastewaters of the chemical industries

TAKE-HOME MESSAGE

● Contamination of surface drinking water with toxic heavy metals is very important.

● The use of industrial or municipal wastewater for irrigation in agriculture is common in many parts of the world.

● For high mercury and aluminum concentrations, the water sources in Dashte Mashhad, Mashhad, northeastern Iran, should not be used for agricultural use.

S. R. Mousavi, M. Balali-Mood, et al

For more informa-tion on the articles of Mandour and Azab seewww.theijoem.com/ijoem/index.php/ijoem/article/view/81andwww.theijoem.com/ijoem/index.php/ijoem/article/view/80

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could be the source of the water wells pol-lution by toxic metals.

Possible sources of contamination were identified as four main irrigation wells, the only wastewater pipe of Toos industrial town and all entering and in-fluent of Parkand-Abad refinery. The en-trance of wastewater pipe to Kashaf river was also sampled. Sampling was done in May 2008, March 2009, and June and July 2010. Water samples were collected in 1-L polyethylene bottles. Nitric acid, as preservative, was added to the containers immediately after collecting the samples. The bottles were then labeled and stored in the refrigerator until testing.

Concentrations of lead, chromium, cadmium and aluminum were measured by atomic absorption spectrometric meth-od using graphite furnace (Perkin Elmer model 3030, USA); mercury and arsenic were measured by a mercury/hydride system. The reliability of the method was evaluated by spiking heavy metals into five samples, determining recovery, de-tection limit and accuracy parameters.26 The accuracy for determination of alumi-num, arsenic, cadmium, chromium, mer-cury and lead were 97.5%, 98.2%, 99.2%, 99.0%, 98.4% and 99.4%, respectively.

The heavy metals levels were com-pared to the maximum permissible levels of heavy metals in agricultural water set by the Food and Agricultural Organiza-tion (FAO).27 The FAO guidelines for mer-cury, lead, chromium, cadmium, alumi-num and arsenic in agricultural water are 1, 500, 100, 10, 100 and 500 µg/L, respec-

tively.Data were analyzed by SPSS® for Win-

dows® ver 11.5 (SPSS Inc, Chicago, Il, USA). Results are presented as mean±SD. A p value <0.05 was considered statisti-cally significant.

Results

A total of 36 samples were collected and examined for the heavy metals. The con-centrations of heavy metals in irrigation water wells and wastewater stations are summarized in Table 1. The mean±SD level of mercury in irrigation water wells (1.02±0.40 µg/L) was more than the per-missible limit (1 µg/L). Since wastewater was used for irrigation, the permissible concentration standards for irrigation water were used. The wastewater samples had a mean±SD mercury contamination of 6.64±2.53 µg/L.

The concentrations of heavy metal concentrations in irrigation water and wastewater changed over time (Figs 2 and 3). The change in aluminum concentra-tion in irrigation water was significantly (p=0.03) changed over time. Concentra-tions of mercury, arsenic, lead and cad-mium in wastewaters also changed sig-nificantly (p<0.05) over time (Fig 3).

Concentrations of mercury and arse-nic in irrigation water and wastewater were compared between each two indi-vidual months and showed significant differences in The concentrations of mer-cury in irrigation water and wastewaters measured in March 2008 were signifi-

Table 1: Mean±SD concentrations of the heavy metals (µg/L) in irrigation water and wastewater samples taken from Dashte Mashhad

Source Mercury Lead Chromium Cadmium Arsenic Aluminum

Irrigation 1.02±0.40 2.61±1.47 7.67±2.59 0.38±0.05 1.32±0.23 26.79±25.18

Wastewater 6.64±2.53 5.50±1.79 11.73±6.93 0.75±0.13 5.05±1.18 480.50±335.55

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Figure 1: Map of the study area. 'I' stands for “irrigation water” and 'W' stands for “wastewater” sampling sites

cantly (p=0.038) different from those in July 2010; the values had also significant (p=0.042) variation from May 2008 to March 2009. The arsenic concentration in wastewaters measured in May 2008 was also significantly (p=0.04) different from that in June 2010.

Discussion

High levels of heavy metals in food result in several acute and chronic health effects. Examples of chronic health problems in-clude cancer, birth defects, disorders of the nervous system, and impairment of the immune system.28 Because of indus-trial and agricultural operations in the study region, there are toxic heavy metals in the groundwater that lead to the con-tamination of drinking water, vegetables and crops; this may in turn cause lead and cadmium-induced diseases (e.g., renal failure) or chromium-induced hair loss.29

Six months sampling from a hospital sewage plant and an industrial plant in Abu Dhabi30 revealed a mercury concen-tration of up to 500 ng/g. Concentrations

of cadmium and lead measured in a local river for irrigation in Shahre Rey, Iran31 were 80 and 60 µg/L, respectively. All these measurements were higher than that found in our study. Concentrations of arsenic, cadmium and chromium in ef-fluents used for irrigation in two parts of India2,3 were 584, 321 and 429 µg/L and 592, 431 and 457 µg/L, respectively; these were also higher than those recorded in our study.

Significant variation observed in the concentrations of mercury and arsenic in wastewaters is probably the result of in-dustrial operations and the subsequent accumulation of pollutants. The wastes of many manufacturers in the region contain mercury. High levels of mercury in irriga-tion water wells are probably originated from the industrial town and the refinery. For the high concentrations of mercury in water wells of this area, it is strongly recommended not to use these wells for agriculture.

Contamination of wastewaters with aluminum is probably due to aluminum blades used in the refinery for stirring

S. R. Mousavi, M. Balali-Mood, et al

For more information on lead exposure and renal function seewww.theijoem.com/ijoem/index.php/ijoem/article/view/51for lead exposure and pregnancy outcome seewww.theijoem.com/ijoem/index.php/ijoem/article/view/94for lead exposure and semen quality seewww.theijoem.com/ijoem/index.php/ijoem/article/view/64

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and treatment of the wastewater. Because of high mercury and aluminum concen-tration in the output of the refinery, the treated wastewater should also not be used for agriculture.

Because the water used for irrigation in Dashte Mashhad, either taken from the wells or refinery wastewaters, are signifi-cantly contaminated with heavy metals—particularly mercury, arsenic and alumi-num, these sources should not be used for agriculture. Furthermore, because of the variance observed in the concentration of heavy metals over months of the year, regular measurements of heavy metals in irrigation water and wastewaters used for agriculture are necessary.

Since the inappropriate waste manage-ment in industrial factories operational in this region is probably the main cause

of contamination of soil and water with heavy metals, more intense audit and monitoring of waste management as well as establishment of new industrial plants in the region should be considered. These industries should consider removing the toxic elements such as mercury from their effluent.

Our study had some limitations. For example, due to some technical difficul-ties and lack of co-ordination between the relevant organizations, it was not possible to carry out samplings regularly. Howev-er, the findings are conclusive.

Acknowledgements

The authors are grateful to Mr. Kazem Es-haghian for his cooperation in sampling and Mrs. Mahdizadeh for her assistance.

Figure 2: Mean concentration of the heavy metals (µg/L) in the irrigation water wells. Error bars represent SD.

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Figure 3: Mean concentration of the heavy metals (µg/L) in wastewaters. Error bars represent SD.

The project was carried out by financial support of the Regional Water Organiza-tion.

Conflicts of Interest: None declared.

References

1. Begum A, Ramaiah M, Harikrishna S, et al. Heavy Metal Pollution and Chemical Profile of Cauvery River Water. e-Journal Chem 2009;6:47-52.

2. Tiwari KK, Singh NK, Patel MP, et al. Metal con-tamination of soil and translocation in vegetables growing under industrial wastewater irrigated agricultural field of Vadodara, Gujarat, India. Eco-toxicology Environ Safety 2011;74:1670-7.

3. Tiwari KK, Dwivedi S, Mishra S, et al. Phytoreme-diation efficiency of Portulaca tuberosa rox and Portulaca oleracea L. naturally growing in an in-

dustrial effluent irrigated area in Vadodra, Gujrat, India. Environ Monit Assess 2008;147:15-22.

4. Mandour RA, Azab YA. The Prospective Toxic Ef-fects of Some Heavy Metals Overload in Surface Drinking Water of Dakahlia Governorate, Egypt. Int J Occup Environ Med 2011;2:245-53.

5. Mandour RA, Azab YA. Toxic Levels of Some Heavy Metals in Drinking Groundwater in Dakahlyia Governorate, Egypt in the Year 2010. Int J Occup Environ Med 2011;2;112-7.

6. Martin MH, Coughtry J. Biological monitoring of heavy metal pollution. London, Applied Science Publishers, 1982.

7. Caussy D, Gochfeld M, Gurzau E, et al. Lessons from case studies of metals: investigating expo-sure, bioavailability, and risk. Ecotoxic Environ Safety 2003;56:45-51.

8. Liu WH, Zhao JZ, Ouyang Z, et al. Impacts of sewage irrigation on heavy metal distribution and contamination in Beijing, China. Environ Int 2005;31:805-12.

S. R. Mousavi, M. Balali-Mood, et al

a r t i c l e

www.theijoem.com Vol 4 Number 2; April, 201386

a r t i c l e

9. Buschmann J, Berg M, Stengel C, et al. Contamina-tion of drinking water resources in the Mekong delta floodplains: Arsenic and other trace metals pose serious health risks to population. Environ Int 2008;34:756-64.

10. Feigin A, Ravina I, Shalhevet J. Irrigation with Treated Sewage Effluent. Berlin, Springer-Verlag, 1991.

11. Urie DH. The status of wastewater irrigation of forest: The Forest Alternative for Treatment and Utilization of Municipal and Industrial Wastes. Seattle, Washington Press, 1986.

12. Yadav RK, Goyal B, Sharma RK, et al. Post-irrigation impact of domestic sewage effluent on compo-sition of soils, crops and ground water- A case study. Environ Int 2002;28:481-6.

13. Horswell J, Speir TW, Schaik AP. Bio-indicators to assess impacts of heavy metals in land-applied sewage sludge. Soil Biol Biochem 2003;35:1501-5.

14. Mapanda F, Mangwayana EN, Nyamangara J, Giller KE. The effect of long-term irrigation using wastewater on heavy metal contents of soils un-der vegetables in Harare, Zimbabwe. Agric Ecosys Environ 2005;107:151-65.

15. Nan Zh, Li J, Zhang J, Cheng G. Cadmium and zinc interactions and their transfer in soil-crop system under actual field conditions. Sci Total Environ 2002;285:187-95.

16. Nyamangara J, Mzezewa J. The effect of long-term sewage sludge application on Zn, Cu, Ni and Pb levels in a clay loam soil under pasture grass in Zimbabwe. Agr Ecosys Environ 1999;73:199-204.

17. Cao ZH, Hu ZY. Copper contamination in paddy soils irrigated with wastewater. Chemosphere 2000;41:3-6.

18. European Commission. Final Report on Heavy Metals in Waste. 2002, Available from http://ec.europa.eu/environment/waste/studies/pdf/heavy_metalsreport.pdf (Accessed February 10, 2002).

19. Vukovic J, Matsuoka S, Yoshimura K, et al. Simultaneous determination of traces of heavy metals by solid-phase spectrophotometry. Talanta 2007;71:2085-91.

20. Shaw M, Haddad PR. The determination of trace metal pollutants in environmental matrices using ion chromatography. Environ Int 2004;30:403-31.

21. Tuzen M, Soylak M. Multi-element coprecipitation

for separation and enrichment of heavy metal ions for their flame atomic absorption spectrometric determinations. J Hazard Mater 2009;162:724-9.

22. Komarek J, Holy J. Determination of heavy metals by electrothermal atomic absorption spectrom-etry after electrodeposition on a graphite probe. Spectrochimica Acta Part B 1999;54:733-8.

23. Boevski I, Daskalova N. Method for determination of toxic and heavy metals in suspended mat-ter from natural waters by inductively coupled plasma atomic emission espectrometry (ICP-AES). Part I. Determination of toxic and heavy metals in surface river water samples. J Univ Chem Tech Metallurgy 2007;42:419-26.

24. Ozturk M, Ozozen G, Minareci O, Minaeci E. Deter-mination of heavy metals in fish, waterand sedi-ments of Avsar Dam Lake in Turkey. Iran J Environ Health Sci Eng 2009;6:73-80.

25. Ning Yu, Li J, Cai W, Shao X. Simultaneous de-termination of heavy metal ions in water using near-infrared spectroscopy with preconcentration by nano-hydroxyapatite. Spectrochimica Acta Part A 2012; 96:289-94.

26. Vahdati N, Balali-Mood M, Timcheh Hariri A, Riahi B. Determination of lead in Mashhad city tap water by graphite furnace atomic absorption spec-trometry. Pharmacologyonline 2011;3:1419-26.

27. Row DR, Abdel-Magid IM. Handbook of waste water reclamation and reuse. CRC Press, 1995.

28. US Committee on the Judiciary. Water Quality Fact Sheet 2: Health Effects of Drinking Water Contami-nants. 1988, Available from www.judiciary.senate.gov/judiciarydocs/CLHDW%20CDR%20Docs/Docs%20(PDFs)/2-1197/CLW/CLW%201861.pdf (Accessed September 25, 2012).

29. Salem HM, Eweida EA, Fraga A. Heavy metals in drinking water and their environmental impact on human health. ICEHM2000, Cairo University, Egypt 2000;542-56.

30. Pillay AE, Yaghi B, Williams JR, Al-Kindy S. Mercury pollution from irrigation with treated sewage water (TSW). J Water Health 2007;5:315-22.

31. Bigdeli M, Seilsepour M. Investigation of Metals Accumulation in Some Vegetables Irrigated with Waste Water in Shahre Rey-Iran and Toxicologi-cal Implications. Am Eurasian J Agric Environ Sci 2008;4:86-92.

Heavy Metals in Irrigation Water Used for Agriculture in Mashhad