This study was conducted on target areas of Bethlehem and Jenin districts (Figure 1). Bethlehem represents the southern area, while Jenin represents the northern area in the west bank.

More than 50 samples of leafy vegetables were collected during late spring of 2018. The vegetable samples were grown on different farms within the study areas. Thirty samples were chosen for analysis. Fifteen of these samples were from Jenin’s farms and fifteen were from Bethlehem farms. Three types of leafy vegetables were taken. These vegetables were Parsley, Spinach, and Arugula.

All collected samples were stored in clean plastic bags and brought to the laboratory for analysis.

Water samples were collected from each site for further analysis; the same water was used for irrigating these vegetables. Water was stored in clean plastic bottles washed with Distilled water. In site, the water bottle was washed with the same irrigating water then was filled with water [24].

In addition, soil samples were taken where the type of soils were terra Rossa in Bethlehem region and grumusols at Jenin zone. However, the soil that was collected was near the roots of the leafy vegetables within 5 to 10 cm depth [25].

Additionally, pesticides samples used on leafy vegetables were also collected for analysis. The samples were stored in clean plastic white bottles that are firmly closed and sent to the laboratory for analysis. Some of the pesticides samples were collected from the farms in both regions, while others were collected from the Ministry of Agriculture in Palestine.

The collected vegetable samples were washed with distilled water to remove dust particles. Then, samples were cut to small pieces. The leafy part was taken, and dried in an oven at 50˚C. After drying, the samples were ready for acid digestion.

For acid digestion, Microwave Digestion System (MARS6) was used which has a great speed, precision and high sensitivity. The method of digestion was given by the machine itself. The weight of each leaf was 0.5 grams. Then 50 ml of 65% pure nitric acid were added to each sample. The mixture was then digested till the transparent solution was achieved. After cooling, the digested samples were filtered using CA sterile syringe filters with 30 mm diameter and pore size of 0.22 µm.

Heavy metals concentrations were determined using Inductively Couples Plasma Mass Spectrometry (ICP-MS) Agilent 7500.

For the soil samples, 50 grams of the soil were weighed and 250 ml of milli-Q water were added. Milli-Q water is ultrapure water as defined by ISO 3696 (Merck Millipore Organization). The processes of purification include many steps of filtration and deionization to reach a purity characterised in term of resistivity 18.2 MΩ∙cm at 25˚C. Milli-Q purifiers produce water pure enough to get accuracy within parts per million (Yokoyama, et al.). Soil samples were kept for fourteen days, so that what surround the soil particles can be tested. This process was performed because it is not the soil particles that need to be analysed but the surroundings of the particles; in other words the leachate. 2 ml of the sample were taken for analysis [25].

In addition, water samples were tested for the metal content by the addition of 65% pure nitric acid. 2 ml of the sample were taken for analysis. Concerning pesticides samples, they were analysed by the use of ICP-MS Agilent 7500 [25].

For accurate quantitative determination of heavy metals in soil, water, vegetables and pesticides, an internal standard method was used using Nd as internal standard and a multi-standard calibration method: 22 metals standard (Ag 10 mg/L, Al 50 mg/L, B 50 mg/L, Ba 10 mg/L, Bi 100 mg/L, Ca 10 mg/L, Cd 10 mg/L, Co 10 mg/L, Cr 50 mg/L, Cu 10 mg/L, Fe 10 mg/L, K 100 mg/L, Li 50 mg/L, Mg 10 mg/L, Mn 10 mg/L, Mo 50 mg/L, Na 50 mg/L, Ni 50 mg/L, Pb 100 mg/L, Sr 10 mg/L, Tl 50 mg/L, Zn 10 mg/L, matrix 5% HNO₃). Samples were prepared by dilution of 1.0 mL of the water samples to 10.0 mL with 0.3% ultrapure nitric acid and analyzed by ICP/MS. Each sample was analyzed three times and the results are expressed as mean ± SD (SD: standard deviation). Relative standard deviation (RSD) of the three results are calculated and found to be less than 5% for all samples for all metals analyzed in this study, reflecting the precision the method for the analysis of these heavy metals. Calibration curves for all metals analyzed were constructed by plotting the ratio of the intensity of the analyze metal to that of the internal standard (Nd) vs. concentration of the trace metal (in ug/L), and results showed that the calibration curves are linear with correlation coefficient (r²) greater than 0.999 for the trace metals analysed [24].

Heavy metals concentrations in green leafy vegetables in Bethlehem region are presented in Table 1. Results revealed variable concentrations of heavy metals in the leafy part of the vegetable samples.

The levels of iron (Table 1) in all vegetables ranged between 25.35 mg/kg and 1569.53 mg/kg. Although leafy vegetables are rich with iron, however, in some samples they exceeded the limit given by WHO/FAO which is 425 mg/kg [20]. In fact, the concentrations of Fe in Batir in arugula and parsley samples are very high, 1045.94 mg/kg and 451.73 mg/kg respectively. The same as in spinach, arugula and parsley samples in Nahaleen, the Fe levels are 1569.53 mg/kg, 546.02 mg/kg, and 567.61 mg/kg respectively. Regarding Lead contents, it varied from 0.03 mg/kg and 1.77 mg/kg. Its concentration levels are relatively high in Batir samples and in Nahaleen. Chromium exceeded the allowable safety limits in arugula samples in two farms, Nahaleen and Batir. Zinc levels ranged from 3.61 mg/kg and 106.5 mg/kg, which is found in arugula sample in Nahaleen. The value is relatively high since the permissible limit given by FAO/WHO is 99.4 mg/kg [20]. Concerning Cadmium, it was found that its concentration in Nahaleen in arugula sample is very high and relatively high in spinach sample. The observed concentrations of Cr, Mn, Co, and Cu lies within the permissible limits set by FAO/WHO.

As for Jenin region, results were quite different from Bethlehem region. Iron,

Lead, Copper and Cadmium revealed relatively high levels in some samples of leafy vegetables. Regarding Iron, its concentration is high in arugula sample located at Zababdeh farm, and relatively high in parsley and spinach sample at the same farm (see Table 2).

Iron concentration was high in three samples taken from the Zababdeh farm (Table 2). The permissible limit set by WHO for Fe is 425 mg/kg. Additionally, it was found that Lead levels of some vegetables sample obtained from Jenin farms exceeded the safe limits established by FAO/WHO for human consumption. The highest concentrations of Pb are 0.32 mg/kg and 0.67 mg/kg; are found in parsley and spinach samples located at Zababdeh farm; and 0.47 mg/kg in parsley sample located at kofr Than farm.

From the present analysis, it can be noticed that Cadmium is relatively high in one of the samples which is spinach at Zababdeh farm. The allowable limit for Cd in leafy vegetables is 0.2 mg/kg (see Table 2) [20]. Similarly to the case with lead in Zababdeh farm.

However, other heavy metals such as Cr, Co, Mn, and Zn contain levels below the WHO/FAO safety limits.

Groundwater in the West Bank from wells and springs is the major source of water being used for irrigation [17].

It was found that all metals for all soil samples in Bethlehem farms and Jenin farms do not exceed the permissible limits given by FAO/WHO. Based on these results, it can be said that no heavy metals contamination in vegetables samples could have resulted from the soil.

In Figure 2 which shows heavy metals concentration in soil samples at Bethlehem region, it can be seen that Fe levels are higher than other metals and its concentration is the highest at Batir. However, it still lies within the allowable limit for soil set by FAO/WHO [20].

It is also noticed that cadmium is not exist in soil samples as well as chromium or have not been detected by the machine due to its low value. In addition, other heavy metals such as Mn, Co, Cu, Pb and Zn are found in very small amounts in the soil.

In Figure 3, it can be seen that Chromium and Cadmium do not exist in these soil samples or they are below the detection limit of the machine. In addition, Fe is the most available heavy metal but does not exceed the permissible limit set by FAO/WHO. It can be also noticed that Manganese exists in Kofr Than farm quite higher compared to other farms. Still, none of these metals is harmful or has any effects within their existed concentrations.

However, when comparing level concentrations of heavy metals in both regions, it can be seen that Fe has the highest value among other elements in all soil samples. Manganese takes the second place then Zinc. All other heavy metals have very low concentrations in soil (see Figure 4). The presented results of heavy metals in soil indicate that heavy metal content in soil is not relevant to heavy metal contamination found in leafy vegetables.

Pesticides samples that were used on leafy vegetables were analyzed for their heavy metals content levels. Table 3 shows some of the used pesticides with their

heavy metal concentration in mg/l. Generally, these pesticide types are the ones often used by farmers when planting and growing leafy vegetables whether in Bethlehem or Jenin regions. Some of these types are used for organic agriculture; others are used as insecticides or nematicide as well as acaricides.

It can be noticed that some metals are presented in relatively high concentration, particularly Iron, Lead, and Zinc. It is noticeable that these concentrations exceeded the permissible limit set by WHO/FAO regarding the presence of heavy metals in pesticides. Obviously, Iron is the most available heavy metal in the pesticides samples used on leafy vegetables. Zinc actually takes the second place regarding its availability in the selected pesticides. Other heavy metals are found in variable amounts as shown in the previous table.

These pesticide types are legal to be used according to the Ministry of Agriculture in the West Bank. Thus using them will not pose a direct problem; however, the validity of such pesticides depends on its concentration and the usage method; whether it is being used in the allowable concentration, or if being diluted correctly, etc.

Additionally, it is important to acknowledge that plenty of pesticides used by Palestinian farmers are illegal according to officials’ statements and controllers at the Ministry of Agriculture. Besides, the smuggled illegal pesticides play a direct role in contamination of vegetables as confirmed by Ministry of Agriculture. Other sources in the West Bank confirm the same statement including the Palestinian Central Bureau of Statistics that reported the excessive use of pesticides where 50% of these pesticides were insecticides. In addition to another institute which is Applied Research Institute Jerusalem (ARIJ) [17] that collected background data about pesticides use in the West Bank, where results had shown widespread problems in both usage and disposal of pesticides. Some of the pesticides used in the West Bank are suspended, cancelled or banned by the World Health Organization [26].

Table 4 shows the generic name of each pesticide along with the concentration of the active ingredient in addition to the category that each pesticide belongs to; it can be noticed that the concentration of the active ingredient varies. These pesticides are found in forms of emulsifiable concentrate, wettable powder, soluble liquid concentrate, soluble powder, suspension concentrate, capsule suspensions, and water dispersible granules.

However, it is quite obvious that the presence of heavy metals in leafy vegetable samples is directly related to the use of some of these pesticides. Probably the pesticides were being mixed wrongly, mishandled and misused. As stated by the Palestinian Central Bureau of Statistics in 2010, the use of pesticides in the West Bank is excessive. Thus, it can be concluded that pesticides have a major role in the contamination found in leafy vegetable samples. Other related Palestinian studies in the West Bank assured that most farmers need more educational programs regarding the safety and the use of pesticides.

To further explain the results, starting with Fe levels in leafy vegetables at Bethlehem region (see Table 1) which is not found in contamination levels

neither in irrigation water or leachate soil, then its presence in vegetables samples mainly in Nahaleen and Batir is related to pesticides appliance. In particular, due to usage of Timor C and Kung Fu Pesticides. As for Pb source, the reason could also be connected to pesticides especially kung Fu, and Defender. Concerning the source of Cr in the same region, it can be linked to the utilization of either Kung Fu, Agriron, or Siperin 10. In addition. Zn levels in Nahaleen Farm is relevant to the use of Timor C or Bio-T plus pesticides. Whereas for Cd levels in Nahaleen, the results leads back to the use of Kung Fu (note the concentrations of heavy metals in Table 4).

Therefore, it can be concluded that the present heavy metal contamination is due to pesticides appliances in the mentioned farms in Bethlehem region. Specifically speaking, samples in Nahaleen and Batir showed high concentrations of heavy metals which were relevant to specific pesticides including Timor C, Kung Fu, Defender, Bio-T, Agriron and Siperin 10. However, the values obtained varied between one vegetable type and the other due to the quantity differences, dilution method, concentration of each pesticide, and the rate of exposure.

Still, there could be a possibility of contamination due to rapid industrialization and urbanization in the above areas in Bethlehem region. Thus, through atmospheric deposits, heavy metals can be absorbed into the plant tissues.

In addition to that, Fe concentration which was observed high in some samples, could be a result of use of iron chelate, which is a soluble complex of iron and chelating agent that is sprayed to plants to treat chlorosis; a condition in which leaves produce insufficient chlorophyll. The high results appeared in plants not in soil samples, because iron chelate is not held by the soil, and does not go under hydrolysis or biodegradation but easily absorbed by the plant. However, this remains a possibility and cannot be assured since there were no collected samples of iron chelate to analyse.

Regarding Jenin region, iron levels exceeded the permissible limits set by WHO/FAO in Zababdeh farm, and the reason for such result was confirmed to be the use of Kung Fu. However, it is noticeable that the used quantity of this pesticide was not the same as in Bethlehem farms since the concentrations were lower compared to those in Bethlehem. Similarly the concentration of lead at Zababdeh farm and Kofr Than farm were the results were also linked to the use of Kung Fu and Defender.

Additionally, copper as apparent in Figure 2 exceeded the limit in Parsley sample at Raba farm. It can be considered that parsley in that farm was exposed to copper containing pesticide though in small portions. These pesticides could include Bio-T plus or Agriron.

In regards to cadmium (see Figure 3), which is relatively high in spinach at Zababdeh farm, the cause for this result could be the exposure of spinach to other types of pesticides but in low portions.

However, it is believed that other farms such as Araneh, Jalameh, Husan, Wad foqin, and AlKhader use pesticides for improving their production but with regards to the allowable limits and according to regulations set by the Ministry of Agriculture. This could be the reason why leafy vegetables in these farms were not contaminated with noticeable heavy metals.

It is important to acknowledge that long term consumption of heavy metal contaminated vegetables may possibly cause numerous health hazards in human. Therefore, regular monitoring of heavy metals is crucial to avoid excessive build-up of these metals in human food chain especially that some pesticides could be illegal; even if legal, some can be misused or misapplied whether by the quantity, exposure rate and duration, or the dilution method.