The arsenic content of forty-one common Malaysian vegetables was analysed by hydride generation-inductively coupled

plasma emission spectrometry. None of the samples showed level greater than 2.00 J.1 g {fJ. The highest was found in

bean sprouts (Phaseolus radiatus) (2.00 J.1 g {fl) and the lowest in sengkuang (Pachyrrhizus erosus) (0.20 J.1 g

{fl). Boiling caused a loss of 17 to 60% arsenic in the plants

Kheng, Lee Chnoong

She, Low Kun

Universiti Putra Malaysia Institutional Repository

Pertanika 15(2), 171-173 (1992)COMMUNICATION IIArsenic Contents in Some Malaysian VegetablesABSTRAKKandungan arsenik dalam empat puluh satu jenis sayur-sayuran yang biasa didapati di Malaysia telah dianalisisdengan menggunakan kaedah pengeluaran hidrida dan spektrometri pancaran atom berjenis plasma bergandingsecara aruhan. Sampel-sampel tersebut tidak mengandungi paras arsenik yang melebihi 2.00 J.1 g {fl. Paras yangtertinggi didapati dalam taugeh, Phaseolus radiatus (2.00 J.1 g {fl) dan yang terendah dalam sengkuang,Pachyrrhizus erosus (0.20 J.1 g {fl). Pendidihan menyebabkan kehilangan sebanyak 17 hingga 60% arsenik dalamtanaman-tanaman tersebut.ABSTRACTThe arsenic content offorty-one common Malaysian vegetables was analysed by hydride generation-inductively coupledplasma emission spectrometry. None of the samples showed level greater than 2.00 J.1 g {fJ. The highest was found inbean sprouts (Phaseolus radiatus) (2.00 J.1 g {fl) and the lowest in sengkuang (Pachyrrhizus erosus) (0.20 J.1 g{fl). Boiling caused a loss of 17 to 60 % arsenic in the plants.INTRODUCTIONAlthough arsenic is generally regarded as a toxicelement (lsinishi et al. 1986), recent work hasshown that it could be an essential trace element.Some studies showed that a trace amount ofarsenic is essential to cell metabolism (Uchus et al.1982). Animals have been shown to be adverselyaffected by dietary arsenic deficiency (Nielson1980). Even though evidence for the essentialityof arsenic as a trace element in humans is lesscompelling, the arsenic content of some Malaysianvegetables was investigated as a possible source ofdietary arsenic. This paper reports the total arsenicin forty-one vegetables and the effect of boilingon arsenic in some of them.MATERIALS AND METHODSVegetables were purchased on three occasions,giving three different samples of each kind ofvegetable, at Seri Kembangan market in 1987.Only the edible portion of the plant was used, toreflect the intake by humans. The plant was washedthoroughly with tap water followed by deionisedwater. More than 600g of vegetable was used. Themoisture content of the plant was determined bydrying in an oven at 80·C. One gram of drypowdered vegetable was digested with a mixtureofHNO/HCI0'1(4:l). Mter digestion it was madeup with 1.2M HCI and analysed for arsenic usinghydride generation-inductively coupled plasmaatomic emission spectrometry as described by Leeand Low (1987). Each sample was analysed induplicate.In order to establish the accuracy of theanalysis, a sample of NBS citrus leaves (No. 1572)was subject to the same treatment.The effect of boiling on arsenic content wasinvestigated with eight vegetables. They were choysam (white stem) (Brassica rapa), cabbage (Brassicaoleracea var. capitata) , wong ngak pak (Brassicachinensis var. pekinensis). bayam hijau (A maranthuspaniculatus), lettuce (Lactuca sativa), waterconvolvulus (Ipomoea reptans), bean sprouts(Phaseolus radiatus) and Chinese kale (Brassicaalboglabra). For this experiment, about 600 g ofthe vegetable was boiled in a glass beaker with2000 ml of deionised water. At intervals of fiveminutes approximately 100g of sample was re-moved and rinsed with deionised water. It wasanalysed for arsenic as described earlier.RESULTS AND DISCUSSIONThe accuracy of the method for arsenic analysiswas established using NBS citrus leaves. The ma-terial in duplicate was treated in the same man-ner as the vegetable samples. Results are shown inTable 1.LOW KUN SHE AND LEE CHNOONG KHENGTABLE 1Analysis of arsenic in NBS citrus leavesTABLE 3Effect of boiling on arsenic content(11 g g.t dry wt) of some Malaysian vegetables0 5 10 15Choy sam (white) 1.61 1.22 0.84 0.72Cabbage 0.36 0.36 0.38 0.34Wong ngak pak 0.34 0.33 0.38 0.37Bayam merah 1.19 1.00 0.73 0.73Lettuce 0.43 0.32 0.25 0.17Water 0.72 0.60 0.60 0.60convolvulusBean sprouts 1.45 1.19 0.96 0.84Chinese kale 0.18 0.14 0.16 0.10The observed value falls within the acceptedvalue, thus establishing the validity of our meth-odology.The arsenic content of forty-one vegetableson a dry weight basis is listed in Table 2. Less than2.00 ug g-l arsenic was found In all vegetables.The highest level was found in bean sprouts(Phaseolus radiatus) (2.00 ~ g g-l) and the lowest insengkuang (Pachyrrhizus erosus), (0.20 ~ g g.I). Thehigh arsenic content in bean sprouts could haveoriginated from the beans or from the water usedin the sprouting process.Although arsenic uptake in general dependson both plant species and element availability,Malaysian vegetables appear to contain relativelylow levels of arsenic. They compare favourablywith uncontaminated leafy vegetables with a rangeof 0.01 to 4.00 ~ g g.l (Wanchope 1983). Higherlevels of arsenic in vegetables have also beenreported but they were grown in arsenic-enrichedsoils. Levels of 3.4 to 10.0 ~ g g.1 have been re-ported (Anderson et al. 1987; Woolson 1973).The effect of boiling on arsenic content inselected vegetables is shown in Table 3.Except for wong ngak pak and cabbage therest of the vegetables show a decrease in arseniccontent upon boiling. In general the amount ofCertified valueObserved valueVegetables3.1±O.32.97±O.09Boiling time (min)arsenic leached is a function of boiling time.Percentage loss after 15 minutes' boiling is from17 to 60%. Loss of other mineral elements invegetables upon boiling has also been observedby other workers. Meiners et al. (1976) reported30 to 50% loss for nine mineral elements in rawand cooked legumes.CONCLUSIONArsenic content in Malaysian vegetables is gener-ally less than 2.00 ug g-I. This compares favour-ably with uncontaminated leafy vegetables reportedby Wauchope (1983). Boiling is effective in re-moving a large percentage of the arsenic in theplants.LOW KUN SHE andLEE CHNOONG KHENGChemistry DepartmentUniversiti Pertanian Malaysia43400 UPM Serdang, Selangor Darnl Ehsan, MalaysiaREFERENCESANDERSO ,L.WJ,J.c. PRINGLE and RJW. RAINES. 1987.Arsenic Levels in Crops Irrigated with WaterContaining MSMA. Weed Sci. 26:370-373.ISINISHI, ., K. TSCHIYA, M. VAHTER and B. FOWLER.1986. Handbook on the Toxicology of Metals.2nd Ed. ed. L. Fribery, G.F. Nordberg and V.Vounk. Elsevier p. 43-83.LEE, C.K. and K.S. Low. 1987. Determination of Ar-senic in Cocoa Beans by Hydride Generationwith ICP-AES. Pertanika 10(1 ):69-73.MEINERS, c.R., N.L. DEVISE, C.H. LAu, M.G. CRESS,J.S.RATCHY and E.W. MURPHY. 1976. The Contents ofNine Mineral Elements in Raw and CookedMature Dry Legumes. J. Agric Food Chem.24(6):1126-1129.NIELSON, F.H. 1980. Evidence of Essentiality of Ar-senic, Nickel and Vanadium and Their PossibleNutritional Significance. In Advances in Nutri-tional Research 3. Ed. H.H. Droper. New York:Menum Press. p. 157.UCHUS, E.D., W.E. CORNATZER and F.H. NIELSE .1982.Evidence for a Possible Function for Arsenic inArginine Metabolism. Fed. Pmc. 41: 783 (Ab-stract) .WANCHOPE, R.D. 1983. Arsenic: Industrial, Biomedi-cal, Environmental Perpectives. ed. W.H. Ledererand RJ Fensterheim, New York: Van NostrandReinhold. p. 342.WOOLSON, EA 1973. Arsenic Phytotoxicity and Up-take in Six Vegetable Crops. Weed Sci. 6:524-527.(Received 13 December 1990).172 PERTAN1KA VOL. 15 NO.2, 1992Scientific nameAllium cepaAmamntlms gangeticusAmamnthus paniculatusAmamnthus spinosusApium graveolensBasella mln-aBenicasa hispidaBrassica alboglabraBrassica chinensisBmssica chinensisBmssica chinensisvar. pekinensisBmssica junceaBmssica oleraceavar. capitataBmssica mpaBmssica rapaCapsicum annumCapsicum annumvar. grossumChrysanthemumcoronariumCucumis sativusCucurbita pepoHibiscus esculentusImpomoea batatasIrnpomoea reptansLactuca indica LLactuca sativaLuJJa acutangulaLycium chinensisLycopersicon esculentumMomordica charantiaNasturtium officinaleNelumbo nuciJeraPachyrrhizus erosusPhaseolus radiatusPhaseolus vulgarisPisum sativumPsophocarpustetragonolobusSaw'opus androgynusSolanum melongenaSpinacia oleraceaVigna sinensis* Mean of three replicatesARSENIC CONTENTS IN SOME MALAYSIAN VEGETABLESTABLE 2Arsenic and moisture content in some Malaysian vegetablesCommon name arsenic* moisture (%)(~ g g-I dry wt)Spring onion 0.59±O.55 91.7Bayam merah 0.60±O.16 91.5Bayam hijau 0.47±O.25 94.8Mar see yin 0.54±O.14 95.7Celery 0.38±O.02 92.6Han choy 0.15 95.0Wax gourd 0.38±O.27 95.3Chinese kale 0.33±O.21 92.2Chinese cabbage 1.94±O.90 94.1Pak choy 0.35±O.08 94.3Wong ngak pak 0.23±O.08 95.8Indian mustard 0.82±O.54 93.0Cabbage 0.26±O.04 94.0Choy sam 0.97±O.32 92.0(green stem)Choy sam 1.17±O.53 93.3(white stem)Chilli (red) 0.27±O.04 82.0Green pepper 0.21±O.09 94.5Tong-ho 0.34±O.08 95.7Cucumber 1.85±O.22 96.4Cheat kuar 0.59±O.47 94.3Lady's fingers 0.48±O.16 91.2Sweet potato 0.99±O.35 91.0leavesWater convolvulus 1.44±O.27 91.5Mak choy 0.28±O.10 92.4Lettuce 0.83 96.2Angled gourd 0.39±O.08 97.0Wolfbery leaves 0.29±O.08 91.5Tomato 0.21±O.12 93.0Bitter gourd 0.29±O.l1 95.6Water cress 0.29±O.07 96.0Lotus root 0.52±O.10 83.1Sengkuang 0.20±O.07 88.1Bean sprouts 2.00±O.65 94.2French bean 0.36±O.09 92.1Green peas 0.15 86.9Four-angled 0.34±O.07 91.5beanShe chai choy 0.77±O.35 82.1Brinjal 0.42±O.13 92.0Spinach 0.28±O.05 93.5String bean 0.48±O.16 90.6PERTANIKA VOL. 15 NO.2, 1992 173

Arsenic Contents in Some Malaysian Vegetables

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Arsenic Contents in Some Malaysian Vegetables

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