- Research article
- Open Access
Spatial distribution of heavy metals in soil, water, and vegetables of farms in Sanandaj, Kurdistan, Iran
© Maleki et al.; licensee BioMed Central Ltd. 2014
- Received: 16 January 2014
- Accepted: 29 October 2014
- Published: 14 November 2014
Heavy metals are ubiquitous elsewhere in nature and their measurement in environment is necessary to develop health management strategies. In this study, we aimed to find out concentrations and spatial patterns of heavy metals in main farms of Sanandaj in Kurdistan, Iran.
Over May to October 2012, six farms were selected to analyze concentrations and spatial patterns of several heavy metals, namely aluminum (Al), arsenic (As), cadmium (Cd), cobalt (Co), chromium (Cr), copper (Cu), nickel (Ni), lead (Pb), and zinc (Zn) in their soil, irrigation water, and edible vegetables. Overall, 36 samples of soil and water and 72 samples of vegetables including coriander (Coriandrum sativum), dill (Anethum graveolens), radish (Raphanus sativus) root and radish leaf were collected. The concentrations of metals were determined by inductively coupled plasma optical emission spectrometry. The spatial surfaces of heavy metals were created using geospatial information system.
The order of metals in soil was Al > Zn > Ni > Cu > Cr > Pb > Co > As > Cd while in water it was Cr > Co > Zn > Pb > Cu > Ni > Al = As = Cd. The order of heavy metals in vegetables was Al > Zn > Cu > Cr > Ni > Pb > Co > As > Cd. Totally, the minimum concentrations of Al, Cu, Pb, and Zn were found in radish root while the maximum of Al, Co, Cr, and Ni were found in radish leaf. The minimum concentrations of Cd and Cr and maximum concentrations of Cu and Zn were also deciphered in dill. Noteworthy, coriander had the minimum concentrations of Co and Ni. The concentrations of Cr and Pb in vegetables were more than maximum allowable limits of the Food and Agriculture Organization (FAO) and the World Health Organization (WHO).
In summary, albeit the concentrations of heavy metals in soil and water samples were below FAO and the WHO standards, vegetables were contaminated by chromium and lead.
- Heavy metals
Heavy metals—those with specific density of about 4-5 g/cm3 or higher—are actually ubiquitous elsewhere in nature. In fact, there are several sources of contamination, namely natural, agricultural, domestic, atmospheric, and other sources . However, tremendous application and utilization of heavy metals in more recent years through industries caused steep emissions to our environment . The main pathways of humans’ exposure to these elements are through air, water, soil and hence agricultural crops .
The health effects of heavy metals have been known since ancient history . In essence, toxicity and/or carcinogenicity of heavy metals, such as lead, arsenic, mercury, cadmium, and nickel have been reported in numerous studies -, even in low dose exposures . In brief, they may cause kidney, lung, nervous system, and skeletal damages, such as itai-itai disease -. Diminished intellectual capacity, gastrointestinal symptoms, coronary heart disease, variety of cancers, such as renal, skin, and bladder cancers, and even death have been also associated with chronic and/or acute exposures to heavy metals ,-.
Some of heavy metals, such as iron, copper, and zinc are present in trace amounts (10 mg/kg, or mg/l) or ultra-trace amounts (1 μg/kg, or μg/l) in environmental matrices as they are essential for biochemical and/or physiological functions. However, quantities beyond the requirement of living organism may lead to its toxicity .
Overall, majority of heavy metals daily intake in humans is from diet, mainly through crop plants ,. It is well recognized now that certain species of plants tend to bioaccumulate heavy metals -. For instance, Maleki and Alasvand Zarasvand  reported that lead, copper, chromium, and cadmium were present in edible vegetables, such as leek, sweet basil, parsley, garden cress, and tarragon in Sanandaj, Iran beyond the allowable national standards. In addition, Mohajer et al.  declared that most plants grown in Isfahan, Iran had heavy metals more than international standards in which 48 and 75 percent of vegetable samples had concentrations of cadmium and lead beyond the Food and Agriculture Organization (FAO) and the World Health Organization (WHO) guidelines. Eslami et al.  determined high levels of cadmium and lead in parsley, leek, radish leaves and roots, and sweet basil, which were well above the maximum threshold values recommended by FAO and the WHO. Pourang and Noori  also analyzed heavy metals in various plant species of an agricultural area near Tehran and reported that chromium, cadmium, and lead were substantially above national and international guidelines in most of vegetables, especially in onions. Cadmium and lead were again principal culprits in cucumbers and bell peppers grown in greenhouses of Qom, Iran . Besides, there are many similar studies from China, Ghana, and other countries that measured heavy metals in agricultural soils, irrigation water and/or their crops -.
The excess presence of heavy metals in edible vegetables that people consume, as reported by numerous researchers, may pose a health threat to general population. Therefore, it is essential to monitor their concentrations in vegetables. Moreover, measurement of heavy metals in irrigation water and also agricultural soil may help to better understand sources of contamination and consequently develop effective management strategies. The application of Geospatial Information System (GIS) technology also has been proposed by other researchers to identify spatial distribution of trace elements and sources of pollution ,. Therefore, in this study, the authors aimed to decipher levels and spatial patterns of heavy metals in soil, irrigation water, and edible vegetables of farms in Sanandaj, Kurdistan, Iran.
Study area and sampling sites
Overall, 18 samples of soil were collected bimonthly during study period (6 farms × 3 times). For each sample at each farm, a mixture of sub-samples was collected to form a composite soil sample to be representative of the whole farm. In detail, a hole of 25 cm was dug using a clean stainless steel trowel and three to four slices of soil from top to bottom were sampled and preserved in a clean bag. The bag was labeled and transferred to the laboratory ,.
Irrigation water sampling
The farms were irrigated by groundwater. Overall, 18 samples of water were collected bimonthly during study period. In detail, sampling was done using a 500 ml washed polypropylene bottle. Noteworthy, 1 ml of nitric acid was added to the samples to avoid microbial activity ,.
The four commonly produced vegetables of these farms were selected for sampling including coriander (Coriandrum sativum), dill (Anethum graveolens), radish (Raphanus sativus) root and radish leaf. Overall, 72 samples of vegetable were compiled bimonthly during study period (6 farms × 4 vegetables × 3 times). A mixture of six sub-samples at various distances (10 m, 30 m, 50 m, 70 m, 120 m and 140 m) was collected for each sample to form a composite sample of vegetables at each farm .
The soil samples were oven dried at 80°C at laboratory until stable weights were obtained. Thereafter, they were crushed using a porcelain mortar with a pestle and mixed thoroughly until they could be sifted through a 10 mesh sieve. For heavy metal analyses, about 100 g of each soil sample was separated out, transferred to a beaker, and as stated in the SW-846, 3050 method of EPA, analytical degree of HNO3 and H2O2 (30%) were applied for soil digestion.
The vegetable samples were transferred to laboratory and washed with distilled water to remove mulch or soil. In order to remove excess moisture, samples were air dried for approximately two weeks. Afterwards, using a porcelain mortar and a pestle, samples were grounded until they could be sifted through a 10 mesh sieve. For heavy metal analyses, about 1 g of each sample was separated out and transferred to a Pyrex beaker. Then, 10 ml of mixture of acids including HNO3, HClO4 and H2SO4 in ratio of 1:1:1 was added to the beaker and maintained at laboratory for 24 hours. After this lag, the beaker was heated at 95°C on hot plate until volume was reduced to 10 ml. Again, 10 ml of acid mixture was added and until reaching to 4 ml was heated. Afterwards, 50 ml of deionized water was added and the digest was filtered. Finally, 100 ml of solution was made by adding double deionized water ,.
The concentration of heavy metals in soil, irrigation water, and vegetables were determined by inductively coupled plasma optical emission spectrometry (ICP-OES) (Model SPECTRO ARCOS, SPECTRO Inc.; Germany). In detail, torch type of apparatus was flared end EOP Torch 2.5 mm; detector was CCD; nebulizer type was cross flow; nebulizer flow was 0.85 l/min; plasma power was 1400 W; coolant flow was 14.5 l/min; and pump rate was 30 RPM. Meanwhile, physicochemical characteristics of soil including pH, EC, total neutralizing value, organic carbon, K, P, soil texture, bulk density, and soil particle percent were analyzed according to the standard methods.
The GIS analysis
All geographic coordinates of sampling points were recorded using a Global Positioning System (GPS) device (Garmin, Garmin International Inc.; Kansas, USA). Next, a GIS was established and using Spatial Analyst extension to ESRI’s ArcMap 9.3 GIS (ESRI, Redlands, CA, USA), spatial surfaces of heavy metals in soil and vegetables were created by interpolation method. The applied interpolation method was Inverse Distance Weighted (IDW).
Descriptive statistics, such as minimum, 25%ile, median, 75%ile, and maximum were presented by box plots. In addition, mean and standard deviation were calculated. We calculated all statistical analyses by STATA software (STATA Corp., TX, USA).
Soil heavy metals
Descriptive statistics of heavy metals in Sanandaj’s soil samples and the international maximum allowable standards
Heavy metal (mg/kg)
Austria standard 
The European Union standard 
Physicochemical characteristics of soil samples in farms of Sanandaj, Kurdistan, Iran
Total neutralizing value (%)
Organic carbon (%)
Bulk density (g/cm3)
Soil particle percent (%)
Irrigation water heavy metals
Descriptive statistics of heavy metals in Sanandaj’s irrigation water samples and the international maximum allowable standards
Heavy metal (ppb)
Austria standard 
Physicochemical characteristics of irrigation water samples in farms of Sanandaj, Kurdistan, Iran a
Total hardness (mg/l CaCO3)
Total alkalinity (mg/l CaCO3)
Vegetables heavy metals
Mean concentrations of heavy metals in Sanandaj’s vegetable samples and maximum allowable standard a
Mean heavy metal (mg/kg)
FAO and the WHO standard 
In this research, we characterized the concentrations of several important heavy metals in agricultural soil, irrigation water, and vegetable crops of six farms in Sanandaj, Kurdistan, Iran. We further depicted spatial distribution of these heavy elements in the studied area.
In general, we know now from our wide literature that levels of each heavy metal in soil is controlled by several interactive complex factors, such as pH, organic matter, cation exchange capacity, clay constitute of soil, and concentrations of aluminum and iron content . More importantly, these factors, especially pH, would affect bioaccessibility and bioaccumulation of these heavy elements in plants. While aluminum is one of the most abundant elements in soil, its availability for crops is dependent on pH ,. It is believed that soluble aluminum, which is absorbable by plants, is present in soil pH below 5.0, where rarely this pH is suitable for agriculture . Noteworthy, aluminum has been classified as a contaminant of potential concern only in soils with a pH of 5.5 or less . This may be the reason why no standard have been set for aluminum in soil (Table 1). However, the unexpected result was that aluminum became the first rank in vegetables of Sanandaj (Table 5 and Figure 3) while pH of soil was circum-neutral to alkaline (Table 2), which means aluminum has been absorbable in soil pH above 5.5. Meanwhile, the minimum and the maximum concentrations of aluminum among the four tested vegetables, respectively, were found in radish root and radish leaf, which means radish leaf may contribute to the maximum intake of aluminum to Sanandaj’s residents through consumption of tested vegetables. Interestingly, the concentration of aluminum in irrigation water samples, which was 0.1 ppm, is much lower than Austria's standard for irrigation water (5000 ppm).
The concentrations of all measured heavy metals in soil and irrigation water were below maximum allowable international standards, while in vegetables the concentrations of chromium (4.2 mg/kg) and lead (0.4 mg/kg) were more than the allowable limits, which are 2.3 and 0.3 mg/kg, respectively (Table 5). The presence of small industries/workshops in the proximity of the farms may be sources of these contaminations. However, this interpretation will be dubious as the concentrations of all heavy metals in soil and water were below the maximum allowable standards. Another reason for lead contamination of vegetables may be that these farms are located near major roads, which may cause air pollution and produce fine particles containing lead. However, it is more than 10 years that pb has been removed from petrol of Iran because of health-related issues . The other interpretation, which is more credible, is presence of Middle Eastern Dust (MED) events in this region ,. In fact, during last decade the welkin of about 11 provinces of Western and South Western Iran have dramatically changed because of MEDs, which is believed originate from deserts of Iraq and Syria ,. Although we could not find any study to date in Sanandaj that evaluate ionic composition of the MEDs, especially heavy metal composition, and as the samples of soil and water were not contaminated by heavy metals, the contamination of vegetables by chromium and lead may be due to the MEDs. In any case, chromium is toxic for most plants and affect seed germination ,. Moreover, chromium compounds have been considered as carcinogen for humans . Long-term exposure to lead, also, is associated with decreases of intelligence capacity in children . Thus, it is essential to inform Sanandaj's population that chromium and lead contaminated vegetables of these farms. In detail, none of the sampled vegetables was safe to human consumption. However, the order of presence for chromium in vegetables was radish leaf > coriander > radish root > dill. For lead, the order was dill = coriander = radish leaf > radish root and radish root had a boundary standard lead content for consumption (Table 5). Overall, radish root and dill had lower concentrations of heavy metals than radish leaf and coriander in Sanandaj. On the other hand, Finster et al.  have found that lead tends to concentrate more in radish roots rather than shoots in Chicago, USA. However, the same was not found in Sanandaj . As shown in Table 5, coriander and dill absorb copper at higher rates than chromium, while for radish root and radish leaf it was reverse. All of the vegetables, except radish root, absorb lead at higher rates rather than cobalt. Meanwhile, all of the vegetables were poor absorber of arsenic and cadmium. It is noteworthy that Sipter et al.  have found that sorrel, carrot, and onion absorb cadmium and zinc at higher rates than lead. Although zinc was the most absorbed heavy metal after aluminum in Sanandaj’s sampled vegetables, lead and cobalt were absorbed at higher rates than cadmium. As illustrated in Figure 4, the vegetables of northeastern farms had more concentrations of aluminum, chromium, copper, and nickel while other measured heavy elements were lower in southwestern sites.
In conclusion, despite the concentrations of measured heavy metals in soil and irrigation water were below the international standards, the concentrations of chromium and lead in vegetables were higher than FAO and the WHO standards.
The authors would like to thank staff of the laboratory at Faculty of Health, Kurdistan University of Medical Sciences, for their wholehearted cooperation. This research was financially supported by Kurdistan University of Medical Sciences; thereby we acknowledge.
- Nagajyoti P, Lee K, Sreekanth T: Heavy metals, occurrence and toxicity for plants: a review. Environ Chem Lett 2010, 8: 199–216. 10.1007/s10311-010-0297-8View ArticleGoogle Scholar
- Nriagu JO: History of global metal pollution. Science 1996, 272: 223–224. 10.1126/science.272.5259.223View ArticleGoogle Scholar
- Järup L: Hazards of heavy metal contamination. Br Med Bull 2003, 68: 167–182. 10.1093/bmb/ldg032View ArticleGoogle Scholar
- Tong S, von Schirnding YE, Prapamontol T: Environmental lead exposure: a public health problem of global dimensions. Bull World Health Organ 2000, 78: 1068–1077.Google Scholar
- Neff JM: Ecotoxicology of arsenic in the marine environment. Environ Toxicol Chem 1997, 16: 917–927.Google Scholar
- Duker AA, Carranza E, Hale M: Arsenic geochemistry and health. Environ Int 2005, 31: 631–641. 10.1016/j.envint.2004.10.020View ArticleGoogle Scholar
- Thompson J, Bannigan J: Cadmium: toxic effects on the reproductive system and the embryo. Reprod Toxicol 2008, 25: 304–315. 10.1016/j.reprotox.2008.02.001View ArticleGoogle Scholar
- Wagner GJ: Accumulation of cadmium in crop plants and its consequences to human health. Adv Agron 1993, 51: 173–212. 10.1016/S0065-2113(08)60593-3View ArticleGoogle Scholar
- Waisberg M, Joseph P, Hale B, Beyersmann D: Molecular and cellular mechanisms of cadmium carcinogenesis. Toxicology 2003, 192: 95–117. 10.1016/S0300-483X(03)00305-6View ArticleGoogle Scholar
- Denkhaus E, Salnikow K: Nickel essentiality, toxicity, and carcinogenicity. Crit Rev Oncol Hematol 2002, 42: 35–56. 10.1016/S1040-8428(01)00214-1View ArticleGoogle Scholar
- Zahir F, Rizwi SJ, Haq SK, Khan RH: Low dose mercury toxicity and human health. Environ Toxicol Pharmacol 2005, 20: 351–360. 10.1016/j.etap.2005.03.007View ArticleGoogle Scholar
- Nishijo M, Nakagawa H, Morikawa Y, Tabata M, Senma M, Miura K, Takahara H, Kawano S, Nishi M, Mizukoshi K: Mortality of inhabitants in an area polluted by cadmium: 15 year follow up. Occup Environ Med 1995, 52: 181–184. 10.1136/oem.52.3.181View ArticleGoogle Scholar
- Hayashi C, Koizumi N, Nishio H, Koizumi N, Ikeda M: Cadmium and other metal levels in autopsy samples from a cadmium-polluted area and Non-polluted control areas in Japan. Biol Trace Elem Res 2012, 145: 10–22. 10.1007/s12011-011-9155-1View ArticleGoogle Scholar
- Weiss B, Clarkson TW, Simon W: Silent latency periods in methylmercury poisoning and in neurodegenerative disease. Environ Health Perspect 2002, 110: 851. 10.1289/ehp.02110s5851View ArticleGoogle Scholar
- Staessen JA, Roels HA, Emelianov D, Kuznetsova T, Thijs L, Vangronsveld J, Fagard R: Environmental exposure to cadmium, forearm bone density, and risk of fractures: prospective population study. Public health and environmental exposure to cadmium (PheeCad) study group. Lancet 1999, 353: 1140. 10.1016/S0140-6736(98)09356-8View ArticleGoogle Scholar
- Kolonel LN: Association of cadmium with renal cancer. Cancer 1976, 37: 1782–1787. 10.1002/1097-0142(197604)37:4<1782::AID-CNCR2820370424>3.0.CO;2-FView ArticleGoogle Scholar
- Lanphear BP, Hornung R, Khoury J, Yolton K, Baghurst P, Bellinger DC, Canfield RL, Dietrich KN, Bornschein R, Greene T: Low-level environmental lead exposure and children’s intellectual function: an international pooled analysis. Environ Health Perspect 2005, 113: 894. 10.1289/ehp.7688View ArticleGoogle Scholar
- Liu J-X, Zhou G-B, Chen S-J, Chen Z: Arsenic compounds: revived ancient remedies in the fight against human malignancies. Curr Opin Chem Biol 2012, 16: 92–98. 10.1016/j.cbpa.2012.01.015View ArticleGoogle Scholar
- Clemens S: Toxic metal accumulation, responses to exposure and mechanisms of tolerance in plants. Biochimie 2006, 88: 1707–1719. 10.1016/j.biochi.2006.07.003View ArticleGoogle Scholar
- Volesky B, Holan Z: Biosorption of heavy metals. Biotechnol Prog 1995, 11: 235–250. 10.1021/bp00033a001View ArticleGoogle Scholar
- Veglio F, Beolchini F: Removal of metals by biosorption: a review. Hydrometallurgy 1997, 44: 301–316. 10.1016/S0304-386X(96)00059-XView ArticleGoogle Scholar
- QuSheng L, ShaSha C, CeHui M, Bei C, LiHua P, FangBing Y: Toxic effects of heavy metals and their accumulation in vegetables grown in a saline soil. Ecotoxicol Environ Saf 2010, 73: 84–88. 10.1016/j.ecoenv.2009.09.002View ArticleGoogle Scholar
- Clemens S, Palmgren MG, Krämer U: A long way ahead: understanding and engineering plant metal accumulation. Trends Plant Sci 2002, 7: 309–315. 10.1016/S1360-1385(02)02295-1View ArticleGoogle Scholar
- Maleki A, Zarasvand Alasvand M: Heavy metals in selected edible vegetables and estimation of their daily intake in Sanandaj, Iran. Southeast Asian J Trop Med Public Health 2008, 39: 335–340.Google Scholar
- Mohajer R, Salehi M, Mohammadi J: Accumulation of cadmium and lead in soils and vegetables of Lenjanat Region in Isfahan Province, Iran. Int J Agronomy Plant Product 2012, 3: 576–578.Google Scholar
- Eslami A, Khaniki GJ, Nurani M, Mehrasbi M, Peyda M, Azimi R: Heavy metals in edible green vegetables grown along the sites of the Zanjanrood river in Zanjan, Iran. J Biol Sci 2007, 7: 943–948. 10.3923/jbs.2007.943.948View ArticleGoogle Scholar
- Pourang N, Noori AS: Assessment of metals in fourteen species of vegetables and crops cultivated in a suburban area using multivariate analyses. Toxicol Environ Chem 2012, 94: 694–712. 10.1080/02772248.2012.672574View ArticleGoogle Scholar
- Aghili F, Khoshgoftarmanesh A, Afyuni M, Schulin R: Health risks of heavy metals through consumption of greenhouse vegetables grown in central Iran. Hum Ecol Risk Assess 2009, 15: 999–1015. 10.1080/10807030903153337View ArticleGoogle Scholar
- Wang L, Guo Z, Xiao X, Chen T, Liao X, Song J, Wu B: Heavy metal pollution of soils and vegetables in the midstream and downstream of the Xiangjiang River, Hunan Province. J Geogr Sci 2008, 18: 353–362. 10.1007/s11442-008-0353-5View ArticleGoogle Scholar
- Wei B, Yang L: A review of heavy metal contaminations in urban soils, urban road dusts and agricultural soils from China. Microchem J 2010, 94: 99–107. 10.1016/j.microc.2009.09.014View ArticleGoogle Scholar
- Akrong MO, Cobbina SJ, Ampofo JA: Assessment of heavy metals in lettuce grown in soils irrigated with different water sources in the Accra metropolis. Res J Environ Earth Sci 2012, 4: 576–582.Google Scholar
- Wang XL, Sato T, Xing BS, Tao S: Health risks of heavy metals to the general public in Tianjin, China via consumption of vegetables and fish. Sci Total Environ 2005, 350: 28–37. 10.1016/j.scitotenv.2004.09.044View ArticleGoogle Scholar
- Bahemuka TE, Mubofu EB: Heavy metals in edible green vegetables grown along the sites of the Sinza and Msimbazi rivers in Dar es Salaam, Tanzania. Food Chem 1999, 66: 63–66. 10.1016/S0308-8146(98)00213-1View ArticleGoogle Scholar
- Karyab H, Mahvi AH, Nazmara S, Bahojb A: Determination of water sources contamination to diazinon and malathion and spatial pollution patterns in Qazvin, Iran. Bull Environ Contam Toxicol 2013, 90: 126–131. 10.1007/s00128-012-0880-8View ArticleGoogle Scholar
- Amini H, Taghavi-Shahri SM, Henderson SB, Naddafi K, Nabizadeh R, Yunesian M: Land use regression models to estimate the annual and seasonal spatial variability of sulfur dioxide and particulate matter in Tehran, Iran. Sci Total Environ 2014, 488: 343–353. 10.1016/j.scitotenv.2014.04.106View ArticleGoogle Scholar
- Hosseini G, Maleki A, Amini H, Mohammadi S, Hassanvand MS, Giahi O, Gharibi F: Health impact assessment of particulate matter in Sanandaj, Kurdistan, Iran. J Adv Environ Health Res 2014, 2: 54–62.Google Scholar
- Sridhara Chary N, Kamala C, Samuel Suman Raj D: Assessing risk of heavy metals from consuming food grown on sewage irrigated soils and food chain transfer. Ecotoxicol Environ Saf 2008, 69: 513–524. 10.1016/j.ecoenv.2007.04.013View ArticleGoogle Scholar
- Weldegebriel Y, Chandravanshi BS, Wondimu T: Concentration levels of metals in vegetables grown in soils irrigated with river water in Addis Ababa, Ethiopia. Ecotoxicol Environ Saf 2012, 77: 57–63. 10.1016/j.ecoenv.2011.10.011View ArticleGoogle Scholar
- Rice E, Baird R, Eaton A, Clesceri L: Standard Methods for the Examination of Water and Waste Water. 22nd edition. American Public Health Association, American Water Works Association, Water Environment Federation, Baltimore; 2012.Google Scholar
- Tiwari K, Singh N, Patel M, Tiwari M, Rai U: Metal contamination of soil and translocation in vegetables growing under industrial wastewater irrigated agricultural field of Vadodara, Gujarat, India. Ecotoxicol Environ Saf 2011, 74: 1670–1677. 10.1016/j.ecoenv.2011.04.029View ArticleGoogle Scholar
- El Bassam N, Tietjen C: Municipal sludge as organic fertilizer with special reference to the heavy metals constituents. In Soil Organic Matter Studies. IAEA, Vienna; 1977.Google Scholar
- McGrath S, Chang A, Page A, Witter E: Land application of sewage sludge: scientific perspectives of heavy metal loading limits in Europe and the United States. Environ Rev 1994, 2: 108–118. 10.1139/a94-006View ArticleGoogle Scholar
- Maleki A, Gharibi F, Alimohammadi M, Daraei H, Zandsalimi Y: Concentration levels of heavy metals in irrigation water and vegetables grown in peri-urban areas of Sanandaj, Iran. J Adv Environ Health Res 2014, 1: 81–88.Google Scholar
- Codex Alimentarius Commission (FAO/WHO): Food Additives and Contaminants, ALINORM 01/12A. 2001:1–289.Google Scholar
- Hernandez L, Probst A, Probst J, Ulrich E: Heavy metal distribution in some French forest soils: evidence for atmospheric contamination. Sci Total Environ 2003, 312: 195–219. 10.1016/S0048-9697(03)00223-7View ArticleGoogle Scholar
- US Environmental Protection Agency: Ecological soil screening level for aluminum. Interim final. OSWER Directive 9285. Washington, DC: 2003:7-60.Google Scholar
- Basta N, Ryan J, Chaney R: Trace element chemistry in residual-treated soil. J Environ Qual 2005, 34: 49–63.Google Scholar
- Mulder J, Rasmussen L, Driscoll C: Aluminum chemistry of acidic sandy soils with various inputs of acidic deposition in The Netherlands and in Denmark. In Environmental Chemistry and Toxicology of Aluminum. Edited by Lewis T. CRC Press; 1989:171-194.Google Scholar
- Finkelstein Y, Markowitz ME, Rosen JF: Low-level lead-induced neurotoxicity in children: an update on central nervous system effects. Brain Res Rev 1998, 27: 168–176. 10.1016/S0165-0173(98)00011-3View ArticleGoogle Scholar
- Givehchi R, Arhami M, Tajrishy M: Contribution of the Middle Eastern dust source areas to PM10 Levels in urban receptors: case study of Tehran, Iran. Atmos Environ 2013, 75: 287–295. 10.1016/j.atmosenv.2013.04.039View ArticleGoogle Scholar
- Gharehchahi E, Mahvi AH, Amini H, Nabizadeh R, Akhlaghi AA, Shamsipour M, Yunesian M: Health impact assessment of air pollution in Shiraz, Iran: a two-part study. J Environ Health Sci Eng 2013, 11: 1–8. 10.1186/2052-336X-11-11View ArticleGoogle Scholar
- Singh HP, Mahajan P, Kaur S, Batish DR, Kohli RK: Chromium toxicity and tolerance in plants. Environ Chem Lett 2013, 1-26.Google Scholar
- Shanker AK, Cervantes C, Loza-Tavera H, Avudainayagam S: Chromium toxicity in plants. Environ Int 2005, 31: 739–753. 10.1016/j.envint.2005.02.003View ArticleGoogle Scholar
- Costa M, Klein CB: Toxicity and carcinogenicity of chromium compounds in humans. CRC Crit Rev Toxicol 2006, 36: 155–163. 10.1080/10408440500534032View ArticleGoogle Scholar
- Finster ME, Gray KA, Binns HJ: Lead levels of edibles grown in contaminated residential soils: a field survey. Sci Total Environ 2004, 320: 245–257. 10.1016/j.scitotenv.2003.08.009View ArticleGoogle Scholar
- Sipter E, Rózsa E, Gruiz K, Títrai E, Morvai V: Site-specific risk assessment in contaminated vegetable gardens. Chemosphere 2008, 71: 1301–1307. 10.1016/j.chemosphere.2007.11.039View ArticleGoogle Scholar
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