International Journal of Application or Innovation in Engineering & Management (IJAIEM) Web Site: www.ijaiem.org Email: editor@ijaiem.org Volume 4, Issue 8, August 2015 ISSN 2319 - 4847 The concentrations of Natural Radioactivity in Pergamum Harmala Seeds Nessrian Ali Hussien Department of Chemical Industries, Institute of Technology- Baghdad ABSTRACT The concentrations of naturallyradioactive occurring and technically enhanced radioisotopes of 10 samples of Peganumharmala insecular equilibrium, collected from different markets in province of Baghdad, have been investigated; using HPGegamma-ray spectroscopy established at low background configuration. Also, the activity concentrations of 40K (1460.81 keV ), 75Se (96.73keV ), 85Kr (513.99 keV), 88Y (1836.01 keV) and 134Cs (563.23 keV, 801.93 keV and 1167.94 keV ) are determined. The average Activity concentrations of the radio elements 40K,75Se, 85Kr and 134Cs in Peganumharmala samples are found to be 425±12.22, 350±10.05, 304±8.73 and 159.17±4.57 Bq/kg respectively, which are below the international global limits. Apparently, the traces of different medium and heavy elements have been investigated using the X-ray fluorescence spectrometer analysis. The measures show the dominant of Potassium-K element in PM samples with the average concentration obtained 53652.62ppm. The other measured traces of the elements indicate a decreasing in the order of K>Fe>Ti>Zr>Nb>Sr>Y>Zn>Ga for the PM samples rather than the order mentioned in reference [37]. Keywords: Pergamum Harmala, concentration of activity, medium and heavy elements, HPGe gamma-ray spectroscopy, X-ray fluorescence spectrometer analysis, 1.INTRODUCTION The Pegamumharmala (PM), family Nitrariaceaecontains mixture of Harmine ,HarmalineNorharman and their derivative, are widely distributed in the central Asia, North Africa, Middle East, South America, Mexico and southern USA [1-5]. It is a wild growing flowering plant in a semi dry condition, steppe areas and sandy soils, native to the eastern Mediterranean region. In the Iraqi tradition different utilizations of PH have been defined, among them, dried grain from this plant are baked in homes to protect against abuse eye and it is applied as an incense to sanctify the air as well as the intellect. Also, In Iraq and other countries expressed concern using the PM extensively for Medical purposes. Different pharmacological research works have shown differentiated effects of PM and /or its active alkaloids in particular the Harmaline [6-10].The Phytochemical studies of PMled to the isolation of different types of chemical ingredients such as alkaloids, steroids, flavonoids, anthraquinones, amino acids, and polysaccharides from its seeds, leaves, flowers, stems and roots [11-13].Among these compounds, the alkaloids,which are found especially in the seeds and the roots, mostly β-Carbolines such as harmine, harmaline, harmalol, harmol and tetrahydroharmine, were found to be the main substances responsible for the antimicrobial, antidepressant, antinociceptive, analgesic, antitumor and vasorelaxant activities of the PM,where the structure of β- carboline alkaloids pays more a tension from biophysical and a medicinal point of view [14-19]. A measurement concentration of the radionuclides for PH amongthe medical and edible plant species has been done by reference [20] and shows the soil-to-plant transfer factor (TF) that the PH had maximum TF (3.17 for 40K). The traces of the heavy metals in PH, among different medical plants collected randomly in polluted and unpolluted areas in Pakistan, have been investigated and monitored by reference [21]. They adopted the dry Ash method with atomic absorption spectrometer to identify the concentrations. Their measurements diagnosedconcentration of iron and nickel elements in PM leaves are about 45.01 (gm/kg) and 19.41 (gm/kg) respectively. In spite of the traditional usage of PH and enormous researches [22-34] that confirmed the possibility use it as a safe and effective therapeutic source in the future, the present work looks after the radioactive concentration in different samples of PH, that collected from different local markets in province of Baghdadas well as, analyzing themain elements in PM using the X-ray diffraction system. 2.EXPERIMENTAL PROCEDURES,RESULTS AND DISCUSION The preparations of the selected 10 PM-samples have been collectedrandomly from different markets in the province of Baghdad in Iraq, see figure (1). These samples are selected for the present research having a wide use in folk medicine for various treatments by local physicians in the area of collection inside Baghdad. These samples are dried for 24 hours in an electric oven at 110 0C to eliminate any traces of water and then, grounded with mortar and pestle. The crushed samples passed through 100 mesh sieve, where further powder and homogeneity are achieved. The sample of 1 kg dry-weight is packed in airtight standard cylindrical plastic container with high geometry 7.6cm x 7.6cm, its area suit the High Purity Germanium (HPGe) detector geometry. The container stored for a period of four weeks before Volume 4, Issue 8, August 2015 Page 45 International Journal of Application or Innovation in Engineering & Management (IJAIEM) Web Site: www.ijaiem.org Email: editor@ijaiem.org Volume 4, Issue 8, August 2015 ISSN 2319 - 4847 counting, so that the secular equilibrium can be attained and the samples subject to gamma spectrometry analysis,where the system is well shielded against the environmental background radiation [35]. The counting analysis is accomplished by using anHPGespectrometryAnalyzer Canberra matched with gamma energies via a library of possible isotopes, through the GENIE2000 program window. The energy resolution of the detector is 8% from the 137Cs energy line at 0.662 MeV, while the activity of the standard at the time of calibration is 25.37kBq.The background spectrum measured under the same conditions for both the standard and sample measurements to correct the calculated sample activityconcentration [36, 37].In a state of secular equilibrium, as shown in figure (2), the activity concentration of the distinguished nuclei found in the typical sample of PM, where the prominent activity concentration of 425 (Bq/kg) found in 40K nuclei with an average energy of the gamma photo peak is1460 keV (10.7%), see table (1), using the following formula: AS Ca Pr M s where,Ca is the net disintegration measured from its γ-line peaks,εγis the system efficiency, Pr is the absolute transition probability of γ- decay and MS is the mass of the sample. Then, following the dominant of 40K- nuclei in the sample, the activity concentrationsof 351 (Bq/kg) and 304 (Bq/kg) from 75Se and 88Y nuclei also have been found through the measurement using the Advanced Gamma spectrometer.The specific activities for the prepared samples are measured for an equal time and minimize uncertainty in background counts (BG).The calculated minimum detectable activity (MDA), is usually based on Curries derivation [38], did by following formula, which implemented within Genie2000: MDA 2.71 4.66 T Y wt where is the standard deviation of the background collected during T time over the energy range of interest, see table (1), at efficiency of the interested energy with branching ratio Y and wt is the sample weight. As shown in table (1) the smallest level of activity that could be detected with confidence, provided that the calculated line minimum detectable activity (LMDA) represents the prior estimation of the best sensitivity that can be expected from PM samples measurements. Also, it can be improved by increasing the detection efficiency of the experimental set up in parallel with decreasing the BG and increasing the time of collection for particular size of the sample. The Handheld X-ray fluorescence spectrometer EDX – Pocket- III analyzer, from Skyray instrument USA, has been used to investigate the main elements in Pergamum HarmalaL. samples. As shown in figure(3) and clearly described in table (1) the concentration (in PPM) for different elements contain in Pergamum Harmala samples using X-ray fluorescence spectrometer. 3.CONCLUSION The gamma spectroscopy method was applied for assessment of the radioactivity traces for different PM samples collected randomly from local markets distributed in Baghdad. The average activity concentrations of 40K (1460.81keV), 75Sc (96.73keV), 85Kr (513.99keV) and 134Cs (563.23keV) in PM samples are found 425±12.22, 350±10.05, 304±8.73 and 159.17±4.57 Bq/kg respectively.On the whole the radionuclide's concentrations are still below the global average of 500 Bq/kg for 40K. The present work also takes interest in tracing different medium and heavy elements in PM samples using the X-ray fluorescence spectrometer analysis. The average concentration recorded higher for the elements K (53652.62ppm), Fe (4218.61ppm) and Ti (990.26 ppm) respectively. The comparison with other [37] shows the iron is not only the dominant elements traced in PM samples, but the present work indicated that the traces of the Potassium element is more dominate in PM samples and show decreasing in the order of K>Fe>Ti>Zr>Nb>Sr>Y>Zn>Ga, as shown in table (1). Acknowledgments The Author is indebted to the Nuclear Group at University of Baghdad/College of Science/ Department of Physics for their assistance in using the nuclear laboratory for measurements. Great thanks and appreciations to the Radiation protection center/ Ministry of Environment and Ministry of Science and technology for their support by using the HPGe System and X-ray fluorescence spectrometer. Volume 4, Issue 8, August 2015 Page 46 International Journal of Application or Innovation in Engineering & Management (IJAIEM) Web Site: www.ijaiem.org Email: editor@ijaiem.org Volume 4, Issue 8, August 2015 ISSN 2319 - 4847 Figure (1): The area where the samples of thePergamum Harmala seeds are collected in Baghdad Province. Figure (2): The Photo peak spectrum measurement of the Pergamum Harmala typical sample using an HP Ge spectrometer at the Radiation Protection Center- Ministry of Environment. The accumulation of counts distinguished the 1460.81keV energy peak for 40K radio nuclei. Table (1): The Line Minimum Detectable Activity concentrations (LMDA)and Activity concentration for different energy levels and radioactive nuclei found in PM sample (Average sample). Nuclide Energy LMDA Activity Nuclide Energy LMDA Activity (keV) (Bq/k) (Bq/kg ) (keV) (Bq/kg) (Bq/kg ) 40 K 1460.8 5.255 425.0 1509.19 26.274 15.083 57 CO 122.06 134.19 7.682 1764.49 4.147 2.380 136.48 91.320 25.822 1847.44 26.192 4.411 60 CO 136.00 757.1 48.386 77.11 7.721 2.622 75 214 Se 96.73 762.67 350.98 PB 87.20 16.225 3.958 85 Kr 513.99 235.75 164.60 241.98 8.039 7.211 88 Y 1836.01 135.34 304.20 295.21 3.033 1.081 134 CS 475.35 142.70 75.947 351.92 1.998 0.196 563.23 26.595 10.634 785.91 82.740 21.621 801.93 33.775 33.362 83.70 2.551 1.925 223 1167.94 244.08 159.17 Ra 338.20 24.156 25.325 208 Tl 510.60 3.850 1.486 83.70 321.4 242.61 224 583.02 0.973 0.215 Ra 240.70 1.5.103 3.290 860.30 8.775 1.224 84.20 52.852 42.044 214 228 BI 609.31 2.033 2.444 Th 63.20 28.199 5.827 Volume 4, Issue 8, August 2015 Page 47 International Journal of Application or Innovation in Engineering & Management (IJAIEM) Web Site: www.ijaiem.org Email: editor@ijaiem.org Volume 4, Issue 8, August 2015 1238.11 1280.96 1377.67 26.806 83.159 19.634 234 4.118 42.770 --- Th 92.30 92.70 ---- --- 21.102 21.795 ---- ISSN 2319 - 4847 8.135 8.402 ---- Figure (3): The concentration for different elements contain in Pergamum Harmala samples, see table (2), using the Xray fluorescence spectrometer. Table(2): The concentrations for different elements (in ppm) for ten samples of Pergamum Harmala. Material’s concentration (ppm) sample K Ti Fe Zn Ga Y Zr Nb Pb Sr PH1 PH2 PH3 PH4 PH5 PH6 PH7 PH8 PH9 PH10 Average 60326.21 49875.35 54677.98 48998.76 59038.93 50034.47 51038.99 51983.01 56001.90 54590.60 53652.62 935.61 1017.02 900.59 1001.25 931.39 1100.01 999.80 1019.8 996.76 1000.31 990.26 4129.23 4155.25 4001.78 4328.28 4420.01 4200.24 4315.63 4267.98 4220.03 4147.67 4218.61 79.78 72.11 82.76 81.22 80.81 84.45 83.61 76.78 82.47 79.41 80.34 28.06 27.28 29.33 30.01 34.62 33.26 35.18 32.78 33.83 33.55 31.79 91.54 89.02 90.91 93.47 94.90 92.71 93.22 90.84 95.21 91.48 92.33 210.87 213.29 209.88 205.81 206.22 207.48 202.89 203.00 204.93 199.13 206.35 197.22 189.59 190.27 184.53 185.65 179.69 186.44 186.20 187.32 174.89 186.18 88.43 89.38 87.51 92.01 90.42 88.82 94.20 90.11 93.89 90.73 90.55 113.28 112.22 114.01 115.29 110.69 111.66 112.53 113.50 110.91 113.61 112.77 REFERENCES [1] Mikaili P., Sharifi M., SHayegh J., Sarahroodi S.H. ,’ Etymological review on chemical and pharmaceutical substances of the oriental origin’,Int J Anim Vet Adv. 2012;4:40–4. 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[34] Herraiz T., González D., Ancín-Azpilicueta C., Arán V.J.,Guillén H. ‘beta-Carboline alkaloids in Peganumharmala and inhibition of human monoamine oxidase (MAO)’, Food ChemToxicol. 2010; 48:839–45. [35] Viruthagiri G. andPonnarasi K., ‘Measurement of natural radio activity in brick samples’, India Advances in Applied Science Research, 2011, 2 (2): 103-108. [36] E. Stranden, Phy. Norv., 1976,8, 167-173. [37] Pourimani R. ,Noori M. , Madadi M., ‘Radioactivity Concentrations in Eight Medicinal and Edible Plant Species from Shazand, Iran’, International Journal of Ecosystem 2015, 5(1): 22-29. [38] Currie L.A., Limits for Qualitative Detection and Quantitative Determination: Application to Radiochemistry, Anal.Chem. 40: 586-593 (1968). AUTHOR Nessrian Ali Hussien received BEng. In Chemical Engineering from London South Bank University 1988, UK Volume 4, Issue 8, August 2015 Page 50