Acta Facultatis Ecologiae - TechnickÃ¡ univerzita vo Zvolene

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157decrease in the following order: Fe, Zn, Pb andCu. The comparison of contamination of individualplant tissues showed that the highest concentrationsof heavy metals have roots and then leavesand stems. Flowers, seeds and fruits have thelowest concentrations of heavy metals. Plant tissuesare considerably damaged at the dump-fieldand increments of year shoots are extremely narrow.Anomalous cell-wall coarsening, occurrenceof calluses, resin canals and numerous hyphaes invessels suggest defense mechanism of plants whichare exposed to stress factors at the dump-field suchas contamination by heavy metals, soil and moisturedeficiency, movement of incohesive materialdown the slope.AcknowledgementsThis work was supported by the Slovak Researchand Development Agency under the contractNo. APVV-51-015605, No. APVV-20-019905 andby Slovak Science Grant Agency under the contractVEGA 1/3256/06.REFERENCES1. KODĚRA, M. et al.: Topografická mineralógia 2.Bratislava : Veda, vydavateľstvo SAV, 1990. 518 s.ISBN 80-224-0101-3.2. ILAVSKÝ, J., VOZÁROVÁ, A., VOZÁR, J.: Ľubietová– štruktúrno-vyhľadávacie vrty Lu-1, L-2a Lu-3. Bratislava : Geologický ústav Dionýza Štúra,1994. 77 s. ISBN 80-85314-32-0.3. BERGFEST, A.: Baníctvo v Ľubietovej na Cu rudu.Banská Štiavnica : Manuskript – Ústredný banskýarchív pre Slovensko, 1951. 89 s.4. HVOŽĎARA, P.: Štúdium zlatých mineralizáciíniektorých jadrových pohorí Západných Karpát.Bratislava : Geofond, 1971. 184 s.5. ROSS, M. et al.: In situ measurment of the aerosolsize distribution in stratospheric solid rocket motorexhaust plumes. In Geophyical Research Letters.1999, roč. 26, č. 7, s. 819–822.6. ĎURŽA, O.: Využitie magnetometrie v environmentálnejgeochémii ťažkých kovov. In Acta GeologicaUniversitatis Comenianae. 2003, roč. 58, s. 29–55.7. CHENG, J., ZHAO, L.: Natural vegetation recoveryon waste dump in opencast coalmine area. In Journalof Forestry Research. 2005, roč. 16, č. 1, s. 55–57.8. DAMIAN, F., DAMIAN, G.: Geochemical characterizationof same old mine waste dumps from BaiaMare area and their influence on the natural vegetation.In Carpathian Journal of Earth and EnvironmentalSciences. 2006, roč. 1, č. 2, s. 63–72.9. SZABADOS, I.: The effect of the precipitation onthe tree ring width. In Carpathian Journal of Eartand Environmental Sciences. 2006, roč. 1, č. 2, s.39–44.10. PETRESCU, L., BILAL, E.: Natural actinides studiesin conifers grown on uranium mining dump (theEast Carpathians. Romania). In Carpathian Journalof Earth and Environmental Sciences. 2006, roč. 1, č.1, s. 63–80.11. BANÁSOVÁ,V.: Rastliny na substrátoch s vysokýmobsahom ťažkých kovov. In Seminár „Ťažké kovyv ekosystéme“. Prešov : BIJO Slovensko, 1996. s.81–94.12. ĎURŽA, O., KHUN, M.: Environmentálna geochémianiektorých ťažkých kovov. Bratislava : PríFUK, 2002. 113 s. ISBN 80-2231-657-1.13. BOWEN, H. J. M.: Environmental chemistry of theelements. London : Academic Press, 1979. 316 s.14. CANNON, H. L.: Botanical prospecting for ore deposits.In Science. 1960, roč. 132 (3427), s. 591–598.15. HAGHIRI, F.: Cd uptake by plants. In J. Environm.Qual. 1973, roč. 2, s. 93–96.16. HOVMAND, M. F.: Plant uptake of airborn cadmium.In Environmental pollution. 1983, roč. 30, č.3, s. 27–38.17. GREGER, M., LINDBERG, S.: Effects of Cd2 2+ andEDTA on young sugar beets (Beta vulgaris) I. Cd 2+uptake and sugar accumulations. In Physiol. Plant.1986, roč. 66, s. 69–74.18. MULLIS, G. L., SOMMERS, L. E.: Characterizationcadmium and zinc in four soils treated with sewagesludge. In J. Environm. Qual. 1986, roč. 15, č. 4, s.382–387.19. PAGE, A. L., BINGHAM, F. T., NELSON, C.: Cadmiumabsorption and growth of various plant speciesas influenced bz solution cadmium concentration. InJ. Environm. Qual. 1972, roč. 1, s. 288–291.20. IMAI, I., SIEGEL, S. M.: A specific response totoxic cadmium levels in red kidney bean embryos. InPhysical Plant. 1973, roč. 29, s. 118–120.21. WEIGEL, H. J., JÁGER, H. J.: Subcellular distributionand chemical form of Cd in bean plants. In PlantPhysiol. 1980, roč. 119, s. 179–189.22. BARCELÓ, J. et al.: Cadmium-induced decrease ofwater stress resistance in bush bean plants (Phaseolusvulgaris L. cv. Contender) I. Effects of Cd on waterpotential. relative water content and cell wall elasticity.In J. Plant Physiol. 1986, roč. 125, s. 17–25.23. FUHRER, J.: Phytotoxic effects of cadmium in leafsegments of Avena sativa L. and the protective roleof calcium. In Experientia. 1983, roč. 39, č. 5, s.525–526.24. PITTER, P.: Hydrochemie. 2. vyd. Praha : SNTL,1990. 568 s. ISBN 80-03-00525-6.25. BENEŠ, S., PABIANOVÁ, J.: Přirozené obsahy distribuceprvků v půdach. Praha : VŠZ, 1987. 202 s.26. LANE, S. D., MARTIN, E. S.: A biochemical investigationof lead update in Raphanas salines. In NewPhytol. 1977, roč. 79, s. 281–286.
15827. LAGERWERFF, J. V.: Uptake of Cd. Pb and Zn byradish from soil and air. In Soil Sci. 1971, roč. 111,č. 2, s. 129–133.28. VIRČÍKOVÁ, E., PÁLFY, P.: Prehľad technológiízneškodňovania nebezpečných odpadov s obsahomarzénu, kadmia a ortuti. In Aktuálne ekologické otázkyE 97. Nebezpečné odpady. Košice : BIJO Slovensko.1997. s. 87–103.29. MATSCHULAT, J.: Arsenic in the geosphere. In Sci.Total Environment. 2000, roč. 249, s. 297–312.
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Acta FacultatisEcologiaeJournal of
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OBSAH / CONTENTSISOL M., MICHALÍKO
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5ACTA FACULTATIS ECOLOGIAE, 16: Sup
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11ACTA FACULTATIS ECOLOGIAE, 16: Su
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19are lower in ill patients compare
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21are considered as the most accura
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24- multimode cavities are usually
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26the load during its exposure to f
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28Tradescantia paludosa 02 test and
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30Tab. 5: Results of positive contr
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35DISCUSSIONThe ionising radiation
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39222Rn is produced by radioactive
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41180160140this reason we also pick
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435001450400350hKz0,8h [m]300250200
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46deposit is that stripped in off-l
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48TruenessTrueness was determined i
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50MATERIAL AND METHODSChloroform (p
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52absorbance [a.u.]1,000,750,500,25
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54Tab. 1: Rrequirements determinati
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56Methods of VOC testing were set a
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59Tab. 6: ContinuedSamples withsurf
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63One of the possible explanations
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65Ai - Ai-1 [Bq.m -3 ]86420-2-4-6-8
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69BiodegradabilityThe great variety
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71degradation starts of late days,
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73Fig. 4 Treated (after 28 days of
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75parameters of the cutting process
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79Fraction: D (residual rest) prese
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81was not confirmed. Maximum of mer
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84Fig. 1 Schematic diagram of atomi
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86Alpha spectrometryAlpha spectrome
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8880007000y = 6622xR 2 = 0.939SIMS
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93Gemer according to the German mod
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95Tab. 1 Results of the chemical an
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97Continuation of Tab. 2 Results of
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99Vlčia Dolina and from the reserv
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101ACTA FACULTATIS ECOLOGIAE, 16: S
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103mg.dm -3mg.dm -35,004,003,002,00
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105year and the average value repre
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Page 110 and 111: 109Sample site 1 Sample site 2 Samp
Page 112 and 113: 111As for the sampling time (Fig. 5
Page 116 and 117: 115Typha latifolia, Carex sp., Scir
Page 118 and 119: 117conditions for decomposition of
Page 122 and 123: 121from the background (derived fro
Page 124 and 125: 12311. PETROVSKÝ, E., ELWOOD, B.:
Page 128 and 129: 1272.52.0Correlation coefficient 0,
Page 132 and 133: 131RESULTS AND DISCUSSIONTable 2 gi
Page 136 and 137: 135V-1 BOREHOLEThe courses of 222 R
Page 138 and 139: 137AV-2 (40m) 2006A ( 222 Rn) [kBq/
Page 140 and 141: 139soaks into the soil, another par
Page 144 and 145: 143Fig. 2 The continuous monitoring
Page 146 and 147: 145Indoor radon activity concentrat
Page 150 and 151: 149Fig. 1 Podlipa dump-fieldCanada)
Page 152 and 153: 151concentrations of Fe. Cu. Cd. Ni
Page 154 and 155: 153DUMP-FIELDREFERENCE SITEppm15001
Page 156 and 157: 155Fig. 5 Compression of wood forma
Page 162 and 163: 161SPECIFIC EXAMPLES OFFACTORS THAT
Page 166 and 167: 165The methods developed to incorpo
Page 168 and 169: 167The effects of wind on ozone con
Page 170 and 171: 169Fig. 6 Mean total and stomatal f
Page 172 and 173: 171transport modelling in North Ame
Page 175: Acta Facultatis Ecologiae, Volume 1
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