Journal of Environmental and Agricultural Sciences (JEAS). Ghanem et al., 2023. 25(3&4):1-10.
Open Access – Research Article
Evaluating Heavy Metals Contamination in Soil, Water and Vegetables Cultivated in Three Areas of Ad-Dawadmi Governorate,
Kingdom of Saudi Arabia
Kholoud Z. Ghanem 1, Mohammed E. S. Abdalla 2 and Ietidal E. Mohamed 1,3*
1University of Shaqra, College of Science and Humanities/ Ad Dawadmi, Department of Biology, Ad-Dawadmi 11911, Kingdom of Saudi Arabia
2University of Khartoum, Faculty of Science, Department of Geology, Khartoum 11115, Sudan
3University of Khartoum, Faculty of Science, Department of Botany, Khartoum 11115, Sudan
Abstract: Irrigation of croplands with untreated wastewater and industrial waste has caused contamination of soils and bioaccumulation of toxic metals in edible parts plants, threatening human health. The concentrations of seven different heavy metals (Cu, Fe, Zn, Ni, Cd, Pb, and Hg) were investigated in the soil, water and the root, fruits and leaf of carrot (Daucus carota), cucumber (Cucumis sativus) and parsley (Petroselinum crispum), collected from three regions; Arjaa, Sajir and Ad-Dawadmi, in Ad-Dawadmi Governorate, Western Riyadh, Kingdom of Saudi Arabia (KSA). The heavy metal contents of the samples were determined after digestion of samples using nitric acid, using Inductively-Coupled Plasma-Mass Spectrometry (ICP-MS). The plant translocation factors (TF) were calculated throughout this study. The results revealed that the concentrations of Cu, Fe, Zn and Ni in all vegetable samples from the three regions were found under the maximum permissible concentration of WHO and FAO Maximum Levels, 73, 425, 99 and 67 [(µg/g) mg/kg], respectively. Concentrations of Cd and Pb in the edible vegetable samples harvested from the Arjaa and Sajir regions are higher than their permissible limits by WHO, 0.36, 0.21; 1.29, and 1.68 with respect to 0.2, 0.3, respectively. Moreover, Hg was not detected in all investigated samples of vegetables, soil and water. Water samples collected from Sajir and Ad-Dawadmi and the soil samples collected from Sajir exceed the standard level of Zn (180, 157 and 103 µg/g respectively). The concentrations of Cd and Pb in the soil and water from the three regions exceed their respective permissible limits. Increased bioaccumulation of certain heavy metals can be a risk factor for consumers in the studied areas. Detailed studies are required to further assess threats of heavy metal contamination in the region.
Keywords: Ad-Dawadmi, Environmental pollution, Heavy metals contamination, soil contamination, toxic metals, vegetable contamination, Kingdom of Saudi Arabia.
*Corresponding author: Ietidal E. Mohamed, email@example.com, firstname.lastname@example.org
Cite this article as:
Ghanem, K.Z., M.E.s. Abdalla and I.E. Mohamed. 2023. Evaluating heavy metals contamination in soil, water and vegetables cultivated in three areas of Ad Dawadmi Governorate, Kingdom of Saudi Arabia. Journal of Environmental & Agricultural Sciences. 25 (3&4): 1-10 [Abstract] [View Full–Text] [Citations].
Copyright © Ghanem et al., 2023 This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium provided the original author and source are appropriately cited and credited.
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Irrigation of croplands with untreated wastewater and application of industrial waste has caused contamination of soils. Crops grown on these contaminated soils cause bioaccumulation of toxic metals in edible plant parts, which transfer to other trophic levels, ultimately to humans, posing a serious risk to human health (Albdaiwi et al., 2022; Noor et al., 2023; Scanlon et al., 2023). Heavy metals are a group of chemical elements including metals and metalloids, having a specific gravity of 4 g/cm3 (Jayakuma et al., 2021), and atomic weight ranges from 63 to 200 Dalton. They can be highly toxic or poisonous to living organisms even at very low concentrations. Generally, these elements do not occur in living organisms and can cause illness (Singh et al., 2023; Velarde et al., 2023).
Heavy metals exist naturally in parent rocks. These rocks are introduced into the environment by natural processes and human activities (Li et al., 2023; Madhav et al., 2023; Nivetha et al., 2023). Anthropogenic activities, such as industrial processes (mining, smelting, various manufacturing processes, incineration, power generation, landfills), agricultural practices (application of fertilizers, manures, pesticides, herbicides fungicides, wastewater, etc), improper waste disposal, emissions from automobiles, land development activities trigger accumulation of heavy metals in the agricultural ecosystems and overall (Jayakuma et al., 2021; Li et al., 2019; Sarhan et al., 2021).
Heavy metal pollution exposure can have serious implications for humans, plants, animals and microbes (Elahi et al., 2018; Farid et al., 2018; Manzoor et al., 2022). Moreover, it can also contaminate soil and water, hindering crop production and animal rearing. It is important to properly manage waste and industrial processes to prevent heavy metal pollution (Sarhan et al., 2021). Chronic health troubles because of exposition to small intensity of heavy metals from natural sources or anthropogenic have become a very important scientific issue globally (Adnan et al., 2022). Uncontrollable vegetables grown in polluted soil can pose serious threats to consumers. Such metals are not able to be degradable and can accumulate in the human body, causing many health problems; one of the major health problems is the different types of cancers (Rehman et al., 2018).
Heavy metals, for instance, lead (Pb) and cadmium (Cd), are the leading environmental pollutants (Zhao et al., 2013; Wen et al., 2022). Even though zinc and copper are essential micronutrients, their existence in the environment in higher concentrations can also be a threat to different plants and humans (Kaur and Garg. 2021; Uchimiya et al., 2020). Pb and Cd have no critical biological functions and are highly noxious to humans (Clemens and Ma, 2016; Collin et al., 2022; Ismael et al., 2018; Qin et al., 2020). The most affected people with heavy metal toxicity are sensitive aged- persons for example pregnant women, the elderly and young children (Alengebawy et al., 2021; Clemens and Ma, 2016). Heavy metal toxicity can cause serious health issues, malfunctioning of the nervous system and could alter blood contents, and damage lungs, kidneys, liver and other fundamental organs (Clemens and Ma, 2016). Consuming food with higher levels of Pb and Cd can critically exhaust the body’s storage of iron, vitamin C and other vital nutrients, causing decreased immunological resistance, intra-uterine development retardation, impaired psycho-social disabilities coupled with malnutrition (Khan et al., 2016; Mohammadi et al., 2018; Mumtaz et al., 2020; Anuoluwa et al., 2021).
The problems of heavy metal contamination of vegetables in the KSA and their accumulation on the vegetables have been reported earlier (Ahmad and Al-Qahtani, 2012; Al Jassir et al., 2005; Arif et al., 2011; Nassar et al., 2018, Khaled et al., 2019). However, the work that has been achieved was concentrated on the problems of heavy metal accumulation on vegetables cultivated in industrial areas or vegetables sold from markets. The Governorate of Ad-Dawadmi northwest Riyadh city, KSA, is a hyperarid area. Water availability is further threatened by changing climatic conditions (Gomaa et al., 2022; Gomaa et al., 2023). Various crops are grown, moreover, livestock and poultry farms are widely distributed all over the area (Al-Zaidi et al., 2011), Main source of irrigation water is the underground water aquifer (Gomaa et al., 2022; Gomaa et al., 2023)
There is no industry, however, a high quantity of heavy metals concentration was observed (Gomaa et al., 2022). Therefore, this study was designed to determine heavy metal concentration loaded in vegetables grown in three farms in Ad-Dawadmi Governorate and to propose future possible improvement measures to reduce the impact associated with the health status of the people and to compare the contamination level of heavy metals in vegetables grown in the three farm regions with the levels that recommended by the international organizations, FAO and WHO. Systematic studies are lacking in the literature to investigate these areas of the KSA for heavy metal contamination in vegetables.
2. Materials and Methods
2.1. Study Area and Geologic History
This study was carried out at three locations of Ad-Dawadmi Governorate, Kingdom of Saudi Arabia (KSA), i.e., Ad Dawadimi town, Arjaa and Sajir (Fig. 1). The area is located northwest of Riyadh Principality, at the highest elevation of the Najd plateau, central KSA.
The region covers an area of about 30,000 km2 with a latitude between 24° 49’ N and a longitude between 44° 13’ E (Hassan et al., 2016). The meteorological data indicated that the annual average rainfall is about 21.4 mm, the summer average temperature is about 41°C and in winter reaches 11°C, and relative humidity ranges between 10 -38%.
The geology of Ad-Dawadmi area is represented by crystalline rocks of the Arabian Shield (Fig. 2) which disappear beneath superficial sediments with some outcrops of different heights scattered in and around the area. The highest altitude in Ad-Dawadmi area is Jabal Al-Nir in the extreme west (about 1307 meters), and in the onward northeast and the lowest plains height is about 660 m. The depths of sedimentary strata are shallow extending between 1.0 and 7.0 m, descending from the west to the east and superimposing with crystalline rocks (El-Didy, 1997). The area is considered part of the Arabian Shield at the east-central boundary, with the Paleozoic sediments, composed of Precambrian granitic rock complexes coupled to two basic complexes and folded meta-sediments strata (Amin and Mesaed, 2023; Gomaa et al., 2022; Gomaa et al., 2023).
2.2. Sampling and Pre-Treatment
Plant samples of harvested fresh vegetables consumed by people were collected from three different farms at Ad-Dawadmi, Arjaa, and Sajir, and these samples were classified into, leafy vegetables (parsley), roots (carrot) and fruits (cucumber) (Table 1). The collected plant samples were kept in containers with treatment and site codes and kept in the laboratory until analyses. Soil (0-25 cm depths) and water samples (three samples) were collected from the same sites and location points where the plant specimens were collected. Individual healthy specimens of each plant sample were selected for chemical analysis. The collected plant species were taxonomically identified.
2.3. Heavy Metal Determination
Soil and water pH were determined using a pH meter. The water and soil collected specimens were digested using HNO3 Conc.: H2O2 (2:1) for the estimation of total heavy metal contents.
Filtration of the treated solutions was carried out using filter paper (Whatman No. 42) and the Inductively-Coupled Plasma-Mass Spectrometry (ICP-MS) was used to analyze collected filtrates for the presence of Cu, Fe, Zn, Ni, Cd, Pb, and Hg. The plant specimens were washed with running tap water and then distilled water to eliminate any soil or debris particles on the outer surfaces of the plants. Subsequently, samples were oven-dried for 72 h at 60o C until constant weight. Samples (0.5 g) were used for digestion using HNO3Conc.: H2O2 (2:1) ratio and heated at boiling water bath. The volume of the obtained digested samples was diluted with distilled water to 25 mL. Filtration of the treated solutions was carried out using filter paper (Whatman No. 42) (Khan et al., 2013). Inductively-Coupled Plasma-Mass Spectrometry (ICP-MS) was used to estimate the amounts of heavy metals in the extracts. To avoid inaccuracy, the results were taken in triplicate. Analytical-grade chemicals were used in this study.
Calibration using standard solutions was made for all elements under estimations. A standard solution (was obtained from Ultra Scientific USA). Using Thermo Scientific- iCAP-Q -Mass Spectrometer model, heavy metal concentrations were recorded against standard solutions. This is achieved by ionizing the sample using an inductively coupled plasma part and then mass spectrometer. The determination of elements using ICP-MS ranges from 7 to 250 atomic mass.
2.4. Metal translocation factor
The transfer of heavy metal from the soil to the plant samples was recorded as a translocation factor (TF). TF was calculated (Cui et al., 2005; Khan et al., 2010) as:
The heavy metal concentrations of the soils and vegetables under investigation were evaluated, in proportion to dry weight. If the TF ratio is greater than one, then the plant accumulates metals, TF ratio=1 indicates no absorption of heavy metals by plants, and if the TF ratio is less than one it indicates a negligible amount of heavy metals absorption (Olowoyo et al., 2010).
3. Results and Discussion
3.1. Heavy Metals Concentrations in Vegetables
In this study trace minerals concentrations such as Cu, Fe, Ni, and Zn and three toxic metals Cd, Hg and Pb were determined in some cultivated vegetables from three regions in Ad-Dawadmi Governorate, KSA, using Inductively-Coupled Plasma-Mass Spectrometry (ICP-MS).
Concentrations of Cu, Fe, Ni and Zn in all vegetable samples from the three regions were found within the maximum permissible concentration (Table 2) 73, 425, 99 and 67 µg/g (mg/kg), respectively. Cadmium values showed mild concentrations against permissible limits by FAO/WHO, 0.2; the lowest value (0.11 µg/g) was recorded from parsley harvested from Arjaa region (Table 2). However, a high Cd concentration was noticed in cucumber (0.26 µg/g) from the same area. The mean concentration levels of Pb in all vegetables of the three regions were detected higher than the permissible limits by FAO/WHO, 0.3 (Table 2); and thus, might be a threat to the consumers.
In this study, Hg was not detected in all samples, vegetables, soil and water. In other words, it might be under an immeasurable level. Plants’ heavy metals contents are affected by some aspects such as rainfall (or water of irrigation), climate, the availability of heavy metals concentration in the area, the soil origin, and finally plants’ status or features during harvesting time (Albdaiwi et al., 2022; Atta et al., 2023). Absorption of mineral nutrients and water is mostly carried out through the plant roots, the direct interaction between the roots, and the surrounding soils which might contain heavy metals, allows the tissues of the plant to absorb different heavy metals within this mineral nutrition (Smical et al., 2008). Later, after the entry of heavy metals inside the roots, they might be either reserved in the storage tissues of the roots or translocated through stems to the other organs of the plant species. Therefore, edible or nonedible parts of the plants could accumulate different concentrations of heavy metals (Arora et al., 2008). The absorption of Pb and Cd by vegetables in the study areas needs much more investigation.
3.2. Heavy metals in soils and waters
The concentrations of Cu, Fe, Zn, and Ni in all soil and water samples from the three regions were found under the maximum permissible concentration (Table 2), except the samples of water from Sajir and Ad-Dawadmi water and soil from Sajir exceeded the standard level of Zn (180, 157 and 103 µg/g respectively). The concentrations of Pb in the soil and water from the three regions exceed their respective permissible limits (Table 2).
Regarding Cd concentration levels from the three regions were found under the maximum permissible concentration only the water sample from Arjaa and the soil sample (Sajir region) were considered above the level of FAO/WHO standards of Cd. Groundwater pollution and higher concentrations of heavy metals (Pb, Cd and Zn) in the three studied areas can be attributed to chemical weathering.
Lead is a critical body poison when cumulative inside the plant body system. It will get inside the plant through air, water and soil and is unable to be removed by rinsing the surfaces of fruits and vegetables (Divrikli et al., 2003). The high concentrations of Pb in these plants are probably attributed to Pb pollutants in irrigation water and/or soil.
3.3. Translocation Factor
Copper exhibited a high translocation factor in almost all samples (TF was more than 1). TF of Fe was recorded as more than 1; for the cucumber collected from Ad-Dawadmi, while Zn was marked as;1.55, and 1.38 µg/g for cucumber and carrot harvested from Arjaa, respectively.
A higher Cd translocation factor was observed for cucumber fruits from the Arjaa area (2.02 µg/g). The soils of the three areas had alkaline pH, despite the high concentrations of Pb in the soil samples, their transfer factor values were low in the given alkaline values. The TF was less than 1 for other metals (Table 3). high TF values may denote that heavy metals are weakly bonded to the soils or efficiently absorbed by vegetables. A Strong bond between heavy metals and colloidal particles in soils may lower TF values.
These results indicated that Cu antagonist Fe, Zn and Cd translocation. Yoon et al., (2006) reported that the mobility of metal may be affected by many factors; soil properties (chemical and physical) and environmental factors. The differences in heavy metals concentration detected in vegetables throughout this study may be due to the solubility of heavy metals in the soil solutions (Cordeiro et al., 2013).
Studied areas lack industrial activities, therefore, the heavy metal pollution can be attributed to geological contamination resulting from the weathering of heavy metal-rich parent rocks and/or human activities (Nazzal et al., 2016). Mineral uptake by plants is influenced by several factors, including their abundance in the soil, water and soil contamination, and proximity of sampling sites to the roads or other sources of pollution (Khan et al., 2015). However, the heavy metals detected in the plants might derive from the soil and/or the irrigation groundwater (Manwani et al., 2023). Obaid et al., (2023) also reported increased levels of heavy matter accumulation in soil, water and plant parts in Afghanistan, when treated with wastewater.
The moderate concentration of Cd is probably because of using a fertilizer that contains Cd or because the area of agriculture is watered with sewage water or both reasons. The high concentrations of Pb in the plant, soil and water need great awareness it conceivably creates real health complications (Natasha et al., 2022; Kumar et al., 2020; Zulfiqar et al., 2019). Our findings are in agreement with the previous reports from different areas of central KSA, by Al Jassir et al., (2005), who detected higher levels of Cd and Pb in some vegetable species collected from central KSA.
The current study results revealed considerable variations in heavy metal concentration were observed in studied vegetables, soil and water samples analyzed. The high concentrations of heavy metals in the samples investigated could fully or partially be referred to as the bedrock texture of the area of the study. The capability of vegetables to mount up metals was emphasized. This study denoted that heavy metals (Zn, Cu, Ni and Fe) were under the permissible standard levels of FAO/WHO level, while Pb and Cd were above the standard level in most plant specimens under the study. One of the obvious results of the present study, the translocation factor of toxic metals by the edible plant samples in the study areas may enhance and consequently be considered a hazard agent for the consumption of these vegetables. To reduce the threats of harmful heavy metals detected, it is better to use nonedible wild plants accumulating pollutants before using soil or land for cultivating vegetables, i.e., phytoremediation. Other studies to confirm these findings might be of great importance.
List of Abbreviations: Cd: Cadmium; Cu: Copper; FAO: Food and Agriculture Organization; Fe Ferrous; Hg: HNO3 Conc.: Concentrated Nitric acid; H2O2: Hydrogen peroxide; Mercury; ICP-MS: Inductively-Coupled Plasma-Mass Spectrometry; mg/kg-: milligram per kilogram: mL: milliliter; µg/g: microgram per gram; Ni: Nickel; Pb: Lead; TF: Translocation Factor; WHO: World health organization; Zn: Zinc.
Competing Interest Statement: The authors have declared that they have no competing interests and there is no conflict of interest exists.
Author’s Contribution: I. E. M. designed the study. I. E. M. and K. Z. G. collected the samples and conducted the experiments. while I. E. M and M. S. A. wrote the manuscript. All the authors read and approved the final manuscript.
Acknowledgment: The authors gratefully acknowledge the Deanship, College of Science and Humanities, Ad-Dawadmi, Kingdom of Saudi Arabia, for the laboratory facilities and materials for experimentation and chemical analysis. No funds were received for this project.
Ahmad, Ali M. H. H. and Kh. M. Al-Qahtani. 2012. Assessment of some heavy metals in vegetables, cereals fruits in Saudi Arabian markets. Egypt. J. Aquat. Res. 38(1): 31-37.
Al Jassir, M.S., A. Shaker and M. A. Khaliq. 2005. Deposition of heavy metals on green leafy vegetables sold on roadsides of Riyadh City. Saudi Arabia. B. Environ. Contam. Tox. 7: 1020-1027.
Albdaiwi, R. N., J. S. Al-Hawadi, Z. B. Al-Rawashdeh, K. A. Al-Habahbeh, J. Y. Ayad and R. S. Al-Sayaydeh. 2022: Effect of treated wastewater irrigation on the accumulation and transfer of heavy metals in lemon trees cultivated in arid environment. Horticulturae. 8: 514.
Albdaiwi, R.N., J.S. Al-Hawadi, Z.B. Al-Rawashdeh, K.A. Al-Habahbeh, J.Y. Ayad and R.S. Al-Sayaydeh. 2022. Effect of treated wastewater irrigation on the accumulation and transfer of heavy metals in lemon trees cultivated in arid environment. Horticulturae. 8: 514.
Alengebawy, A., S.T. Abdelkhalek, S.R. Qureshi and M.-Q. Wang. 2021. Heavy metals and pesticides toxicity in agricultural soil and plants: Ecological risks and human health implications. Toxics. 9: 42.
Al-Zaidi, A.A., E.A. Elhag, S.H. Al-Otaibi, and M.B. Baig, 2011. Negative Effects of Pesticides on the Environment and the Farmers’ Awareness in Saudi Arabia: A Case Study. J. Anim. Plant Sci. 21: 605–611.
Amin, A.A., A.A. Mesaed, . 2023. The Role of the Geologic and the Geomorphologic Factors in the Formation of Some Geotourism Sites of Saudi Arabia, in: M. Allan, R. Dowling (Eds.) Geotourism in the Middle East. Springer International Publishing, Cham, pp. 193-234.
Anuoluwa, I.A., B.E. Oyinloye, O.P. Ogunmola. 2021. Heavy Metals Contamination of Arable Lands: A Threat to Food Security and Safety, in: O.O. Babalola (Ed.) Food Security and Safety: African Perspectives, Springer International Publishing, Cham, pp. 791-806.
Arif, I. A., H.A. Khan, A.A. Al Homaidan and A. Ahamed. 2011. Determination of Cu, Mn, Hg, Pb and Zn in the outer tissues washings, outer tissues and inner tissues of different vegetables using ICP-OES. Pol. J. Environ. Stud. 20(4): 835-841.
Arora, M., B. Kiran, S. Rani, A. Rani, and B. Kaur, et al. 2008. Heavy metal accumulation in vegetables irrigated with water from different sources. Food Chem. 111: 811–815.
Atta, M. I., S. S. Zehra, D.-Q. Dai, H. Ali, K. Naveed, I. Ali, M. Sarwar, B. Ali, R. Iqbal, S. Bawazeer, U. K. Abdel-Hameed and I. Ali. 2023. Amassing of heavy metals in soils, vegetables and crop plants irrigated with wastewater: Health risk assessment of heavy metals in Dera Ghazi Khan, Punjab, Pakistan. Front. Plant Sci. 13: 1080635.
Atta, M.I., S.S. Zehra, D.-Q. Dai, H. Ali, K. Naveed, I. Ali, M. Sarwar, B. Ali, R. Iqbal, S. Bawazeer, U.K. Abdel-Hameed, I. Ali. 2023. Amassing of heavy metals in soils, vegetables and crop plants irrigated with wastewater: Health risk assessment of heavy metals in Dera Ghazi Khan, Punjab, Pakistan. Front. Plant Sci. 13 (2023).
Clemens, S. and J.F. Ma. 2016. Toxic heavy metal and metalloid accumulation in crop plants and foods. Ann. Rev. Plant Biol. 67: 489-512.
Collin, S., A. Baskar, D.M. Geevarghese, M.N.V.S. Ali, P. Bahubali, R. Choudhary, V. Lvov, G.I. Tovar, F. Senatov, S. Koppala and S. Swamiappan. 2022. Bioaccumulation of lead (Pb) and its effects in plants: A review. J. Hazard. Mat. Lett. 3: 100064.
Cordeiro, F., L. Baer, P. Robouch, H. Emteborg, and S.Z. Can, et al. 2013. Setting maximum limits for trace elements in baby food in European legislation: The outcome of International Measurement Evaluation Programme®-33. Food Addit Contam Part A. Chem Anal Control Expo Risk Assess. 30: 678–686.
Cui Y.J., Y.G. Zhu, R.H. Zhai, Y. Huang, Y. Qiu and J. Liang. 2005. Exposure to metal mixtures and human health impacts in a contaminated area in Nanning, China. Environ Int. 31, 784-790.
Divrikli U., S. Saracoglu, M. Soylak, and L. Elci. 2003. Determination of trace heavy metal contents of green vegetable samples from Kayseri- Turkey by flame atomic absorption spectrometry. Fresen. Environ. Bull. 12: 1123–1125.
Elahi, N., I. A. Rehmani, A. Majeed and M. Ahmad. 2018. Salicylic acid improves physiological traits of Zea mays L. seedlings under copper contamination. Asian J. Agric. Biol. 6: 115-124.
El-Didy S. 1997. Evaluation of The Proposed Drainage Network for Lowering the Groundwater Levels in Al-Dawadmi Town. J. King Abdulaziz Univ. Environ. Arid L. Agric. Sci. 8: 111–123.
FAO/WHO. 2001. Codex alimentarius twenty-fourth session, Geneva, Switzerland, 2-7 July 2001. ALINORM 01/12, Joint FAO/WHO Food Standards Programme, Geneva, Switzerland.
Farid, M., S. Ali, M. Rizwan, Q. Ali, R. Saeed, T. Nasir, G. H. Abbasi, M. I. A. Rehmani, S. T. Ata-Ul-Karim, S. A. H. Bukhari and T. Ahmad. 2018. Phyto-management of chromium contaminated soils through sunflower under exogenously applied 5-aminolevulinic acid. Ecotoxicol. Environ. Saf. 151: 255-265.
Gomaa, H.E., A.A. Alotibi, M. Charni and F.A. Gomaa. 2023. Integrating GIS, statistical, hydrogeochemical modeling and graphical approaches for hydrogeochemical evaluation of Ad-Dawadmi ground water, Saudi Arabia: status and implications of evaporation and rock-water interactions. Sustainability. 15: 4863.
Gomaa, H.E., M. Charni, A.A. Alotibi, A.H. AlMarri and F.A. Gomaa. 2022. spatial distribution and hydrogeochemical factors influencing the occurrence of total Coliform and E. coli bacteria in groundwater in a hyperarid area, Ad-Dawadmi, Saudi Arabia. Water. 14: 3471.
Hassan, I., A.R. Ghumman, H.N. Hashmi. 2016. Global warming and temperature changes for Saudi Arabia. J. Biodivers. Environ. Sci. 8: 179-191.
Hu, Y., D. Wang, L. Wei, X. Zhang and B. Song. 2014. Bioaccumulation of heavy metals in plant leaves from Yan׳an city of the Loess Plateau, China, Ecotoxicology and Environmental Safety, 110 (2014) 82-88.
Ismael, M.A., A.M. Elyamine, M.G. Moussa, M. Cai, X. Zhao, C. Hu. 2018. Cadmium in plants: uptake, toxicity, and its interactions with selenium fertilizers. Metallomics. 11: 255-277.
Johnson, P.R. 2006. Explanatory notes to the map of Proterozoic geology of western Saudi Arabia: Saudi Geological Survey Technical Report SGS-TR-2006-4, 62 p., 22 figs., 2 plates.
Kaur, H. and N. Garg. 2021. Zinc toxicity in plants: a review. Planta. 253: 129.
Khaled F.S., A.R. Muhammad, A.A. Al Mulla and O.A. Labib. 2019. Heavy metals in some date palm fruit cultivars in Saudi Arabia and their health risk assessment. Int. J. Food Prop. 22(1): 1684-1692,
Khan S., S. Rehman, A.Z. Khan, A.M. Khan and M.T. Shah. 2010. Soil and vegetables enrichment with heavy metals from geological sources in Gilgit, northern Pakistan. Ecotoxicol. Environ. Saf. 73: 1820-1827.
Khan, A., S. Javid, A. Muhmood, T. Mjeed, A. Niaz and A. Majeed. 2013. Heavy metal status of soil and vegetables grown on peri-urban area of Lahore district. Soil Environ. 32(1): 49-54.
Khan, A., S. Khan, M. Alam, M.A. Khan, M. Aamir, Z. Qamar, Z.U. Rehman and S. Perveen. 2016. Toxic metal interactions affect the bioaccumulation and dietary intake of macro- and micro-nutrients. Chemosphere. 146: 121-128.
Khan, A., S. Khan, M.A. Khan, Z. Qamar, M. Waqas. 2015. The uptake and bioaccumulation of heavy metals by food plants, their effects on plants nutrients, and associated health risk: a review. Environ. Sci. Pollut. Res. 22: 13772-13799.
Kumar, A., A. Kumar, C.-P. M.M.S., A.K. Chaturvedi, A.A. Shabnam, G. Subrahmanyam, R. Mondal, D.K. Gupta, S.K. Malyan, S.S. Kumar, S. A. Khan, K.K. Yadav, Lead Toxicity: Health Hazards, Influence on Food Chain, and Sustainable Remediation Approaches, International Journal of Environmental Research and Public Health, 17 (2020) 2179.
Li, Q., X. Li, C. Bu, P. Wu. 2023. Distribution, risk assessment, and source apportionment of heavy metal pollution in cultivated soil of a typical mining area in Southwest China. Environ. Toxicol. Chem. 42: 888-900.
Madhav, S., R. Mishra, A. Kumari, A.L. Srivastav, A. Ahamad, P. Singh, S. Ahmed, P.K. Mishra, M. Sillanpää. 2023. A review on sources identification of heavy metals in soil and remediation measures by phytoremediation-induced methods. Int. J. Environ. Sci. Technol. https://doi.org/10.1007/s13762-023-04950-5.
Manwani, S., P. Devi, T. Singh, C.S. Yadav, K.K. Awasthi, N. Bhoot and G. Awasthi. 2023. Heavy metals in vegetables: a review of status, human health concerns, and management options. Environ. Sci. Pollut. Res. 30: 71940-71956.
Mohammadi, M.J., A.R. Yari, M. Saghazadeh, S. Sobhanardakani, S. Geravandi, A. Afkar, S.Z. Salehi, A. Valipour, H. Biglari, S.A. Hosseini, B. Rastegarimehr, M. Vosoughi and Y. Omidi Khaniabadi. 2018. A health risk assessment of heavy metals in people consuming Sohan in Qom, Iran. Toxin Rev. 37: 278-286.
Mumtaz, S., S. Ali, R. Khan, H.A. Shakir, H.M. Tahir, S. Mumtaz, S. Andleeb. 2020. Therapeutic role of garlic and vitamins C and E against toxicity induced by lead on various organs. Environ. Sci. Pollut. Res. 27: 8953-8964.
Nassar O.M., H.A. Nasr, M.H. El-Sayed and A.A. Kobisi. 2018. Heavy Metal Levels in Some Popular Vegetables from Some Selected Markets in Saudi Arabia. Egypt. J. Bot. 58 (3):627 – 638.
Natasha, M. Shahid, S. Khalid, M. Saleem. 2022. Unrevealing arsenic and lead toxicity and antioxidant response in spinach: a human health perspective. Environ. Geochem. Health. 44: 487-496.
Nazzal, Y., F.K. Zaidi, B.A. Abuamarah, I. Ahmed, F.M. Howari, M. Naeem, N.S.N. Al-Arifi, M.K. Jafri and K.M. Al-Kahtany. 2016., Evaluation of metals that are potentially toxic to agricultural surface soils, using statistical analysis, in northwestern Saudi Arabia. Environ. Earth Sci. 75: 171.
Nivetha, N., B. Srivarshine, B. Sowmya, M. Rajendiran, P. Saravanan, R. Rajeshkannan, M. Rajasimman, T.H.T. Pham, V. Shanmugam, E.-N. Dragoi. 2023. A comprehensive review on bio-stimulation and bio-enhancement towards remediation of heavy metals degeneration. Chemosphere. 312: 137099.
Noor, R., A. Maqsood, A. Baig, C.B. Pande, S.M. Zahra, A. Saad, M. Anwar, S.K. Singh. 2023. A comprehensive review on water pollution, South Asia Region: Pakistan. Urban Clim. 48: 101413.
Obaid, H., L. Ma, S. E. Nader, M. H. Hashimi, S. Sharifi, H. Kakar, J. Ni and C. Ni, 2023: Heavy Metal Contamination Status of Water, Agricultural Soil, and Plant in the Semiarid Region of Kandahar, Afghanistan. ACS Earth Space Chem. 7: 1446-1458.
Olowoyo, J.O., E. Van Heerden, J.L. Fischer and C. Baker. 2010. Trace metals in soil and leaves of Jacaranda mimosifolia in Tshwane area, South Africa. Atmos. Environ. 44: 1826–1830.
Qin, S., H. Liu, Z. Nie, Z. Rengel, W. Gao, C. Li, P. Zhao. 2020. Toxicity of cadmium and its competition with mineral nutrients for uptake by plants: A review. Pedosphere. 30: 168-180.
Scanlon, B.R., S. Fakhreddine, A. Rateb, I. de Graaf, J. Famiglietti, T. Gleeson, R.Q. Grafton, E. Jobbagy, S. Kebede, S.R. Kolusu, L.F. Konikow, D. Long, M. Mekonnen, H.M. Schmied, A. Mukherjee, A. MacDonald, R.C. Reedy, M. Shamsudduha, C.T. Simmons, A. Sun, R.G. Taylor, K.G. Villholth, C.J. Vörösmarty, C. Zheng. 2023. Global water resources and the role of groundwater in a resilient water future. Nat. Rev. Earth Environ. 4: 87-101.
Singh, V., N. Singh, S.N. Rai, A. Kumar, A.K. Singh, M.P. Singh, A. Sahoo, S. Shekhar, E. Vamanu, V. Mishra. 2023. Heavy metal contamination in the aquatic ecosystem: toxicity and its remediation using eco-friendly approaches. Toxics. 11: 147.
Smical, A., V. Hotea, V. Oros, J. Juhasz and E. Pop. 2008. Studies on transfer and bioaccumulation of heavy metals from soil into lettuce. Environ. Eng. Manag. 7(5): 609–615.
Uchimiya, M., D. Bannon, H. Nakanishi, M.B. McBride, M.A. Williams and T. Yoshihara. 2020. Chemical speciation, plant uptake, and toxicity of heavy metals in agricultural soils. J. Agric. Food Chem. 68: 12856-12869.
Velarde, L., M.S. Nabavi, E. Escalera, M.-L. Antti, F. Akhtar. 2023. Adsorption of heavy metals on natural zeolites: A review. Chemosphere. 328: 138508.
Wen, M., Z. Ma, D. B. Gingerich, X. Zhao and D. Zhao. 2022. Heavy metals in agricultural soil in China: A systematic review and meta-analysis. Eco-Environ. Health. 1: 219-228.
Yoon, J., X. Cao, Q. Zhou and L. Ma. 2006. Accumulation of Pb, Cu, and Zn in native plants growing on a contaminated Florida site. Sci. Total Environ. 368(2–3): 456–464.
Zhao, X.-f., L. Chen, M. I. A. Rehmani, Q.-s. Wang, S.-h. Wang, P.-f. Hou, G.-h. Li and Y.-f. Ding. 2013. effect of nitric oxide on alleviating cadmium toxicity in rice (Oryza sativa L.). J. Integ. Agric. 12: 1540-1550.
Zulfiqar, U., M. Farooq, S. Hussain, M. Maqsood, M. Hussain, M. Ishfaq, M. Ahmad and M.Z. Anjum. 2019. Lead toxicity in plants: Impacts and remediation. J. Environ. Manag. 250: 109557.