Volume 19(1), 126- 129, 2015 JOURNAL of Horticulture, Forestry and Biotechnology www.journal-hfb.usab-tm.ro Researches regarding rubidium content in soil and plants using analysis by atomic fluorescence X-ray Alda S.1*, Alda Liana Maria1, Cristea T.1, Gogoasa I.1, Negrea P.2, Danci M.1, Gergen I.1 1 University of Agricultural Sciences and Veterinary Medicine of Banat "King Mihai I of Romania" Timisoara; ”Politehnica University” -Timisoara, Romania 2 *Corresponding author. Email: [email protected] Abstract The increased concern for reduction of environmental pollution has stimulated continuing research on the toxicology of heavy metals. The content of rubidium in soils is largely inherited from the parent rock, as is indicated by the highest mean Rb contents 100 to 120 ppm, in soils over granites and in alluvial soils. Rb apparently is easily taken up by plants, as are other monovalent cations. The aim of this study was to determine rubidium uptake in Agropyron repens and Cirsium arvense, in a polluted area, using analysis by atomic fluorescence X-ray. This is a modern method of determination of mineral elements, for environmental samples, geological, biological (solid and liquid) without processing. Our results regarding rubidium contents in soil and sudied plants are higher than those obtained by other researchers. Agropyron repens and Cirsium arvense, accumulated rubidium in their tissues diferently. The preliminary results can be used as informative data that they will be confirmed by further analysis by absorption atomic spectrometry method (FAAS), an specific method for determining such elements. The increased concern for reduction of environmental pollution has stimulated continuing research on the toxicology of heavy metals. The rubidium content in soils is largely inherited from the parent rock, as is indicated by the highest mean Rb contents 100 to 120 ppm, in soils over granites and in alluvial soils. Rb apparently is easily taken up by plants, as are other monovalent cations. Most of the higher plant species analyzed by the researchers contained Rb in the range of 20 to 70 ppm (DW), Alfalfa (98 ppm) and Grass (130 ppm). Rubidium has no known biological role and is non-toxic. However, because of its chemical similarity to potassium we absorb it from our food, and the average person has stores of about half a gram. It is slightly radioactive and so has been used to locate brain tumours, as it collects in tumours but not in normal tissue [2,3,4,9,13,14]. Phytoremediation consists of mitigating pollutant concentrations in contaminated soils, water, or air, with plants able to contain, degrade, or eliminate metals, pesticides, solvents. Bioaccumulation factor and translocation factor can be used to give a clue on the suitability of the plant in question in phytoremediation. This is because phytoremediation technology uses the potential of heavy metal bioaccumulation of plants to clean up heavy metal polluted areas. The possibility of “phytoremediation” is suggested to reduce the radionuclides in soil [1,15]. 126 Key words atomic fluorescence X –ray, rubidium, soil, Agropyron repens, Cirsium arvense, polluted area Cirsium arvense is a weed known for high capacity of storage of heavy metals [12]. The aim of this study was to determine rubidium uptake in Agropyron repens and Cirsium arvense, in a polluted area, using analysis by atomic fluorescence X-ray. In order to exploit the natural potential of Agropyron repens and Cirsium arvense in accumulating of rubidium and depleting the soil radioactivity, seven samples of each plant species were tested under laboratory conditions. Cirsium arvense is considered a “problemweed” that can be met again, year after year, in all the Romania’s regions, covering almost 65.00% of the cereal crops. In Romania, Cirsium arvense can be found in almost all the crops, being considered one of the most damaging weeds existent in our country. Agropyron repens (Couch grass) is a plant of wild flora, the family Gramineae, widespread in Europe and Asia. In Romania grows on cultivated land and fallow, sandy or clay soils in meadows, grasslands, arid coast, roadsides and forests, from plains to the mountain area [7,10]. Analysis by atomic fluorescence X-ray is a modern method of determination of mineral elements, for environmental samples, geological, biological (solid and liquid), without processing. The soil and plants samples were taking from a industrial area: Tarnaveni (Mures County, Romania)Figure 1. Material and Methods Fig. 1.Tarnaveni area (Photo: Alda Simion) Seven location area were taken into our study. From each sampling site we took soil and plants samples. The samples soil pH values ranged between 7,61-8,03. The soil samples collected from the 0-40 cm depth were air dried, crushed, passed through a 2 mm mesh sieve and stored at ambient temperature for analysis. All the collected samples of plants were washed with double distilled water to remove airborne and soil pollutants. After washing, plants samples were oven dried at 80°C to constant weight. The soil and whole plant samples were ground and packed in polyethylene bags of 10 grams. We used analyzer spectral fluorescence ray X (FRX), model NITON XL3t GOLD +, with basic features: tube miniaturized X-ray, anode silver, X-ray detector SDD-type Si, NDT specific software package operating systems. Measurements were carried out by applying the measurement window of the device directly on the surface of the polyethylene bags of samples. The levels of the mineral elements analyzed, expressed as ppm (mg/kg dry matter). were read directly from the screen of the device. The transfer factors were calculated using formula: TF = concentration of metal in edible part/concentration of metal in soil [5]. Results and Discussions The experimental data obtained for the rubidium detected by using atomic fluorescence X-ray are shown in Figure 2. The tested plants accumulated rubidium in their tissues differently. 127 Rubidium contents(ppm) 90 80 70 60 50 40 30 20 10 0 Site 1 Site2 Site3 Soil Site4 Site5 Cirsium arvense Site6 Site7 Agropyron repens Fig. 2. Rubidium contents in soil and plants samples (ppm) In figure 3 are presented the transfer factors values for Cirsium arvense and Agropyron repens regarding rubidium uptake. 0,25 0,2 0,15 0,1 0,05 0 Site1 Site2 Site3 Site4 Cirsium arvense Site5 Site6 Site7 Agropyron repens Fig. 3. Transfer factor values Conclusions The experimental data obtained for the rubidium are higher than those obtained by other researchers [8], maybe the differences are due to the different environment conditions and the different analysis method. 128 Our results confirm the fact that Cirsium arvense possessed the characteristics of accumulator of heavy metal. We must consider that in studied area, plants leaf pollution can be caused by heavy metal dust reaching the surface foliar brought by air currents. The preliminary results can be used as informative data that they will be confirmed by further analysis by atomic absorption spectrometry (FAAS), an specific method for determining such elements. Acknowledgments Paper publishing was funded by the project "Teaching staff in pre-university education and the public university - promoter of lifelong learning," POSDRU/174/1.3/S/149155”, co-financed by the European Social Fund through the Sectorial Operational Program for the Human Resources Development 2007–2013. References 1. Baker, A.J.M., Walker, P.L., 1990- Ecophysiology of metal uptake by tolerant plants: heavy metal tolerance in plants. In Shaw, A.J. (ed.), Evolutionary aspects. CRC Press, Boca Raton, pp. 155–177. 2. Bordean D.M., Borozan A.B., Pirvulescu L., Iancu T., Popescu R., Filimon N.M., Moigradean D., Gergen I., 2013- Enrichment of soils: Plaque or aid? 13th SGEM GeoConference on Ecology, Economics, Education And Legislation, Conference Proceedings, Vol. 1, pp 361 - 368 . 3. Bordean D.M, 2010 -„Ecologie si protectia mediului”, 175 pagini; Editura Eurobit, Timisoara 4. Cârciu G., 2006 – Managementul lucrărilor solului, Ed. Eurobit, Timisoara, 5. Cui, Y.L., R.H. 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