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Pakistan Journal <strong>of</strong> Science (Vol. 61 No. 4 December, 2009)INVESTIGATION OF TRACE ELEMENTS IN VEGETABLESF. Deeba, Z. Iqbal, S. Rehman, A. Inayat and A. Habib *Applied Chemistry Research Center *Center for Environmental Protection Studies, PCSIR Laboratories Complex LahoreABSTRACT: Three <strong>vegetables</strong> tori (Luffa acutangula), kaddu (Cucurbita pepo) and br<strong>in</strong>jal(Solanum meongena) were collected from four different places. Vegetables collected from PCSIRcolony, Taj Bagh, Railway road and Mandi S<strong>in</strong>gh Pura were represented by 1, 2, 3 and 4 respectively.The samples were digested with hydrochloric acid and perchloric acid. After filtration andsubsequently volume was made for analysis. Trace <strong>elements</strong> Fe, Zn, Mn, Cu and Cr were <strong>in</strong>vestigatedby atomic absorption spectrophotometer Maximum concentration <strong>of</strong> Fe, Cu, Zn, Mn and Cr wererecorded <strong>in</strong> Tori-1 (13 mg/kg), Tori-4 (0.49mg/kg), Kuddu-1 (4.5 mg/kg), Tori-3 (1.4 mg/kg) andBr<strong>in</strong>-2 (0.69 mg/kg) respectively. While m<strong>in</strong>imum concentration for Fe, Cu, Zn, Mn, and Cr werefound <strong>in</strong> Kaddu-4 (3.24 mg/kg), Br<strong>in</strong>-2 (0.25 mg/kg), br<strong>in</strong>-2 (3.22 mg/kg), Kaddu-4 (0.72 mg/kg) andTori-2 (0.15 mg/kg) respectively.Key words: Vegetable, Trace <strong>elements</strong>, Atomic absorption spectrophotometer, Digestion, PerchloricacidINTRODUCTIONVegetables are staple part <strong>of</strong> human meal takenas food <strong>in</strong> raw or cooked forms. Over the past fewdecades, there has been a change <strong>in</strong> the focus <strong>of</strong>nutritional, health concerns from malnutrition to widespread chronic shortages <strong>of</strong> micronutrients. Theirdeficiency may cause serious functional disorders(Anthony et al., 2007). Trace <strong>elements</strong> are <strong>in</strong>organic<strong>com</strong>pounds, which are essentially required for normalmetabolism (Achterberg, 1994). These m<strong>in</strong>erals arerequired <strong>in</strong> m<strong>in</strong>ute quantities (Kaplan et al., 1993). Theyhave tendency to accumulate <strong>in</strong> human vital organs overprolonged period <strong>of</strong> time lead<strong>in</strong>g to unwanted side effects(Sathawara et al., 2004). The excess and deficiency <strong>of</strong>micronutrients may produce undesirable effects. Excess<strong>of</strong> these nutrients <strong>in</strong> food are associated with number <strong>of</strong>diseases especially with cardiovascular, kidney, nervousas well as bone diseases (Steenland and B<strong>of</strong>fetta, 2000,lamp, 2003). The deficiency <strong>of</strong> <strong>trace</strong> metals also causediseases like impaired immune functions, gastro<strong>in</strong>test<strong>in</strong>aldistress, muscular pa<strong>in</strong>s etc (Paul et al., 1997).Therefore determ<strong>in</strong>ation <strong>of</strong> metal content <strong>in</strong><strong>vegetables</strong> is important from view po<strong>in</strong>t <strong>of</strong> crop yield,food nutrition and health impacts. The requirement <strong>of</strong><strong>vegetables</strong> <strong>in</strong> our daily diet must be 300-350 gm perperson as these conta<strong>in</strong> large quantities <strong>of</strong> Vitam<strong>in</strong>s,Carbohydrates, essential am<strong>in</strong>o acids and dietary fibers,which are required for normal function<strong>in</strong>g <strong>of</strong> human(WHO, 1998).Lead, copper, z<strong>in</strong>c and iron concentrate <strong>in</strong> thesoil and water and ultimately leads to the <strong>vegetables</strong>(Ghafoor and Manzoor, 2004). Metallic uptake has beenwidely <strong>in</strong>vestigated throughout the world. Metals usuallyenter the food cha<strong>in</strong> from water to soil and then to plantroots (Chaney et al., 1998). Z<strong>in</strong>c and cadmium werefound <strong>in</strong> <strong>vegetables</strong> (Ansari and Kazi, 1999). Heavymetals <strong>in</strong> edible green <strong>vegetables</strong> grown along the sites <strong>of</strong>rivers were estimated <strong>in</strong> Iran (Eslami et al., 2007).Factors affect<strong>in</strong>g the uptake <strong>of</strong> heavy metals <strong>in</strong> <strong>vegetables</strong><strong>in</strong>cludes nature <strong>of</strong> soil, application <strong>of</strong> fertilizers and waterirrigated (Anyanwa et al., 2004). Keep<strong>in</strong>g <strong>in</strong> view <strong>of</strong> theimportance <strong>of</strong> the role <strong>of</strong> heavy metals play <strong>in</strong> def<strong>in</strong><strong>in</strong>gthe nutritional status <strong>of</strong> human body, the present studywas <strong>in</strong>itiated to <strong>in</strong>vestigate the level <strong>of</strong> heavy metals FeCr, Cd, Mn, Zn and Cu <strong>in</strong> <strong>vegetables</strong>. The level <strong>of</strong> abovecited metals were <strong>in</strong>vestigated by atomic absorptionmethod <strong>in</strong> three <strong>vegetables</strong> abundantly consumed by thelocal population.MATERIALS AND METHODSVegetables Tori (luffa acutangula), Kaddu(curcurbita pepo) and Br<strong>in</strong>jal (solanum meongena) werecollected from four different places. The numbers 1, 2, 3and 4 were assigned to <strong>vegetables</strong> collected from PCSIRcolony, Taj Bagh, railway workshop and S<strong>in</strong>gh Puramandi, respectively (Table 1). Collection <strong>of</strong> <strong>vegetables</strong>was carried out <strong>in</strong> the similar conditions i.e. same day andsame season. Samples were collected randomly andstored <strong>in</strong> polyethylene bags previously treated with 10%HNO 3. All samples were separately washed with distilledwater to elim<strong>in</strong>ate air borne pollutants. Stakes and leaveswere separated from all samples and slices <strong>of</strong> <strong>vegetables</strong>were made. These samples were air-dried on sheet <strong>of</strong> apaper to remove excess moisture. Then samples were195


Pakistan Journal <strong>of</strong> Science (Vol. 61 No. 4 December, 2009)dried <strong>in</strong> oven at 80°C for one hour. Precisely weighed (2g each) samples were ground <strong>in</strong> mortar and thensubjected to wet wash<strong>in</strong>g and digested with HNO 3:HCLO 4 <strong>in</strong> the ratio <strong>of</strong> 2:1.Table-1. Vegetables and their collection sites.Name Code given Collection locationLuffa Acutangula Tori1 PCSIR ColonyTori2Taj BaghTori3 Railway WorkshopTori4 Mandi S<strong>in</strong>gh PuraCucurbita pepo Kaddu I PCSIR ColonyKuddu2 Taj BaghKuddu3 Railway WorkshopKuddu4 Mandi S<strong>in</strong>gh PuraSolanummeongenaBr<strong>in</strong>l PCSIR ColonyBr<strong>in</strong>2Taj BaghBr<strong>in</strong>3 Railway WorkshopBr<strong>in</strong>4 Mandi S<strong>in</strong>gh PuraAfter digestion samples were filtered with 0.45~m pore size cellulose nitrate membrane filter paper andvolume made up to 100 ml with distilled water. Thesamples were stored <strong>in</strong> airtight conta<strong>in</strong>ers for elementalanalysis through atomic absorption spectrophotometer for(Eslami et al., 2007). Atomic absorptionspectrophotometer (Hitachi polarized Zeeman Atomicabsorption spectrophotometer) was used along-with sixstandard solutions (0.1-2.5 mg/I). . Flow rate <strong>of</strong> air andacetylene 17.0 l/m<strong>in</strong> and 2.0 l/m<strong>in</strong> were adjusted andanalysis was performed accord<strong>in</strong>gly. Metal contents werecalculated by <strong>com</strong>parison with the standard curve <strong>of</strong>respective metals. Specific hollow cathode lamps wereused for each metal at their respective wavelength. Thedata thus collected were subjected to statistical analysisthrough ANOVA technique (Steel et al., 1997).RESULTS AND DISCUSSIONThe concentrations <strong>of</strong> Fe, Cu, Mn, Zn and Crwere observed <strong>in</strong> three <strong>vegetables</strong> collected from fourdifferent locations. The results (Table 2) showed thatmaximum concentration <strong>of</strong> Fe, Cu, Zn, Mn and Cr. wererecorded <strong>in</strong> Tori-l (13 mg/kg), Tori-4 (0.49mg/kg),Kuddu-l (4.5 mg/kg) Tori-3 (1.4 mg/kg) and Br<strong>in</strong>-2 (0.69mg/kg) respectively. While m<strong>in</strong>imum concentration forFe, Cu, Zn, Mn, and Cr were found <strong>in</strong> Kaddu-4 (3.24mg/kg), Br<strong>in</strong>-2 (0.25 mg/kg), br<strong>in</strong>-2 (3.22 mg/kg),Kaddu-4 (0.72 mg/kg) and Tori-2 (0.15 mg/kg),respectively. Iron: Maximum concentration <strong>of</strong> iron wasfound <strong>in</strong> Tori 1 (13 mg/kg) followed by Kaddu 1 (6.31mg/kg) and Br<strong>in</strong> 1(5.5mg/kg). Iron act as catalyst <strong>in</strong> bodyand present <strong>in</strong> greater than any other <strong>trace</strong> element. Ironis the most abundantly found element <strong>in</strong> the human body,Table-2. Analysis <strong>of</strong> <strong>trace</strong> <strong>elements</strong> <strong>in</strong> Vegetables.SamplecodesTori 1Tori 2Tori 3Tori4Br<strong>in</strong>.1Br<strong>in</strong>.2Br<strong>in</strong>.3Br<strong>in</strong>.4Kaddu IKaddu 2Kaddu 3Kaddu 4FeMg/kg13.0 a± 0.5667.1 be±0.1417.8 b±0.4246.2 cd±0.5655.5 de±0.4244.3 f±0.8485.12 ef±0.0985.06 ef±0.0846.31 cd±0.4385.4 de±0.5654.13 fg±0.0983.248 g±0.169CuMg/kg0.46 a±0.0420.39 a±0.0280.40 a±0.0980.49 a±0.0560.39 a±0.0710.25 a±0.0710.3 a±0.0280.48 a±0.0560.46 a±0.0710.40 a±0.0140.36 a±0.0710.45 a±0.056ZnMg/kg3.88 abc±0.8482.6 de±0.7073.5 bed±0.1413.9 ab±0.4243.4 f±0.0283.22 bcde ±0.1692.31 e±0.0712.93 ede ±0.1134.5 a±0.5652.72 de±0.1472.71 de±0.1272.7 de±0.141MnMg/kg1.3 ab±0.1411.3 ab±0l.4 a±0.4241.3 ab±0.1411.3 ab±0.4241.12 ab±0.0561. 0 ab±1.2401.13 ab±0.0421. 04 ab±0.0561.1 ab±0.4240.96 ab±0.0710.72 b±0.098CrMg/kg0.35 b±0.0420.15 b±0.0560.36 b±0.0280.48 b±0.0980.65 b±0.0840.69 b±0.0710.60 b±0.1410.60 ab±1.4120.42 b±0.0560.38 b±0.0560.46 b±0.0140.51 b±0.071The means with the different superscripts <strong>in</strong> a columndiffer significantly (P≤ 0.05)accord<strong>in</strong>g to estimate hemoglob<strong>in</strong> and myoglob<strong>in</strong>conta<strong>in</strong>s 57.6% and 8.9% iron respectively (Jacob et aI.,1974). National research council re<strong>com</strong>mended the dailydietary allowance <strong>of</strong> iron for male is 10-12 mg and forfemale 15 mg and the re<strong>com</strong>mended limit <strong>of</strong> iron was upto 30mg (Kaplan et aI., 1993). Our <strong>vegetables</strong> conta<strong>in</strong>iron content more as <strong>com</strong>pared to Nigerian <strong>vegetables</strong>(Anthony et al., 2007) and less than Poland and Iran<strong>vegetables</strong> (Buszewski et aI., 2000 and Mohsen andSeilsepour, 2008).Z<strong>in</strong>c: The maximum concentration <strong>of</strong> z<strong>in</strong>c was found <strong>in</strong>Kaddu 1 (4.5 mg/kg) and m<strong>in</strong>imum was <strong>in</strong> Kaddu 4(2.7mg/kg) (Table- 2). Z<strong>in</strong>c is the second abundant <strong>trace</strong>metal <strong>in</strong> the human body. Z<strong>in</strong>c is important for enzymaticaction. Normal body conta<strong>in</strong>s 1.4- 2.3 gm <strong>of</strong> z<strong>in</strong>c and itresent <strong>in</strong> all body cells. Re<strong>com</strong>mended daily deity <strong>in</strong>take<strong>of</strong> z<strong>in</strong>c is about 15 mg for adult male and 12 mg forfemale (Kaplan et aI., 1993). It was less than determ<strong>in</strong>ed<strong>in</strong> reddish root, sp<strong>in</strong>ach, green pepper and tomato thatconta<strong>in</strong>63.15, 297.40,61.36 and 46.20 ppm respectively(Mohsen and Seilsepour, 2008). It was also less than theNigerian and Iranian <strong>vegetables</strong> (Anthony et al., 2007196


Pakistan Journal <strong>of</strong> Science (Vol. 61 No. 4 December, 2009)and Eslami et al., 2007).Copper: The maximum concentration <strong>of</strong> copper metalwas found <strong>in</strong> Tori 4 (0.49 1 mg/kg), and Kadddu(0.46mg/kg) m<strong>in</strong>imum was <strong>in</strong> Br<strong>in</strong> 2 0.25 mg/kg (Table2). Normal biological activities <strong>of</strong> am<strong>in</strong>o acids andtyros<strong>in</strong>ase enzymes require copper as an essential <strong>trace</strong>metal. Excessive <strong>in</strong>take <strong>of</strong> copper may cause haemolysis,hepatotoxic and nephlotoxic effects. The mean daily<strong>in</strong>take <strong>of</strong> copper from UK total dietary studies (TDS) fellfrom 2.3 mg per person to less than 1.6 mg per person(Watson et aI., 1993), whereas accord<strong>in</strong>g to an estimate1.5 -3.0 mg/day <strong>of</strong> dietary copper has been determ<strong>in</strong>e tobe safe and adequate for human consumption (Kaplan etal., 1993). This content was less than <strong>vegetables</strong> studied<strong>in</strong> Indian which conta<strong>in</strong>l2.3 mg/kg (Lokeshwari andChandrappa, 2006). It was also less than Poland andIranian <strong>vegetables</strong> (Buszewski et al., 2000 and Mohsenand Seilsepour, 2008).Manganese: The maximum concentration <strong>of</strong> manganesewas found <strong>in</strong> Tori 3 (1.4 mg/kg), Br<strong>in</strong> 1 (1.3mg/kg) andKaddu 2 (1.lmg/kg). In mammals and poultry,Manganese is essential for normal growth, skeletalformation and for normal reproductive function. Theestimated safe and adequate daily dietary <strong>in</strong>take <strong>in</strong> adultsis 11 mg/day (Kaplan et al., 1993). This content was lessthan Iranian <strong>vegetables</strong> like reddish root 130mg/kg, dill37.51 mg/kg, coriander 43.95 mg/kg and tomato 14.93mg/kg (Mohsen and Seilsepour, 2008).Chromium: The maximum concentration <strong>of</strong> chromiumwas found <strong>in</strong> br<strong>in</strong> 2 (0.69 mg/kg), Kaddu 4 (0.51 mg / kg)and Tori 4 (0.48 mg/ kg) Table 2. Chromium is present <strong>in</strong>human tissues <strong>in</strong> variable concentration and its deficiencycharacterized by disturbance <strong>in</strong> glucose, lipid and prote<strong>in</strong>metabolism (Underwood, 1971). The US Nationalacademy <strong>of</strong> sciences has re<strong>com</strong>mended 50200 kg, whereas for UK total dietary study (TDS) copper <strong>in</strong>take limitfor chromium was 136 kg (Kaplan et. al., 1993).This content was greater <strong>in</strong> our <strong>vegetables</strong> as<strong>com</strong>pared to Iranian and Nigerian <strong>vegetables</strong> (Eslami etal., 2007 and Haliru et al., 2009). Similarly high level <strong>of</strong><strong>trace</strong> <strong>elements</strong> <strong>in</strong> the <strong>vegetables</strong> from Iran, Egypt andGreece were reported (Samarghandi et al., 2000,Dogheim et al., 2004, Karavoltsos et al., 2002)respectively. 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