47RESULTS AND DISCUSSIONFor validation of the process of the new developedcoupling FTC-GFAAS were chosen threedifferent feeding <strong>vo</strong>lumes of the sample and completevalidation set were survey for all feeding <strong>vo</strong>lumes.The linear range, limit of detection and limitof quantification were appointed, respectively. Finallywere assessed repeatability, reproducibilityand accuracy by analyzing the standard referencematerial.Linear rangesLinear ranges are summarized in Tab. 1. Listedresults show broad ranges, parameters of the calibra-tion curves, coefficients of determination and regressioncoefficients for different feeding <strong>vo</strong>lumes.Limit of detection (LOD) and limitof quantification (LOQ)Assessed values for limit of detection and limitof quantification for determination of Sb (III) arelisted in Tab 2.RepeatabilityFig. 3 represent the dependence of measuredconcentration of the Sb(III) against measurementorder (significance level 0,05, selected concentrationwas 20 µg.dm –3 ). Repeatability characterizedby RSD was 1.8 % (n = 20).Tab. 1 Linear ranges, equations of the linear regressions and their coefficients for different feeding <strong>vo</strong>lumes Sb(III)Feeding <strong>vo</strong>lume[ml]Linear range[µg·dm –3 ]Equation of regression R 21 4,2–800 τ = 1,467+0,268*c 0,99935 1,2–250 τ = 6,184+1,229*c 0,997010 0,4–250 τ = 6,434+2,690*c 0,9958Tab. 2 Summarized values of slopes and increments for assessement of LOD and LOQ over ULA-2 aproach [7]<strong>vo</strong>lume [ml] LOD [µg.dm –3 ] LOQ [µg.dm –3 ] Equation of regression1 1,4 4,20 τ = 0,637+0,208*c5 0,39 1,17 τ = 0,480+1,703*c10 0,12 0,36 τ = –0,024+2,948*c20Sb(III) 20g.dm -3 , RSD = 1,8% for (n=20)concentration g.dm -31510501 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20measurementsFig. 3. Repeatability of the determination of the Sb(III) (ρ = 20 µg.dm –3 , feeding <strong>vo</strong>l. 2 ml)
48TruenessTrueness was determined in standard referencematerial CRM 12-3-10 by on-line FTC-GFAAS ofthe total Sb.The FTC-GFAAS technique developed at theseconditions have some limitations. It is suitable onlyfor determination of Sb(III) species and total Sbmust be converted to the Sb(III) form. Many publicationswere pointed to the selective reduction oftotal Sb to Sb(III) form. As appropriate procedurefor selective reduction step seems to be utilizingL-cysteine [8].CONCLUSIONSThe aim of this work was to develop an on–linecoupling of electrochemical preconcentration to theAAS method and the utilization of the developedsystem for the determination of ultra-trace amountsof Sb in water samples. The flow-through electrochemicalanalyzer EcaFlow (model GLP 150, Istran,Bratislava) was used as the preconcentrationunit with a two-electrode cell. The working electrodewas a RVC electrode coated with gold. TheAAS spectrometer Spectraa 400 with the graphitefurnace atomizer (Varian) was used to measure thepreconcentrated Sb species. The preconcentrationparameters for the electrochemical process wereoptimized. The deposition runs at a constant currentof –8000 µA and the optimum stripping currentwas found to be 150 µA.The deposition was made from the hydrochloricacid solution, which was then on-line replacedby a diluted nitric acid facilitating the AAS measurementof Sb. The advantage of the used preconcentrationsystem was in an automatic and reliablematrix exchange facility. Optimum electrolyte concentrationswere found to be 1 mol.dm –3 HCl and2 mol.dm –3 HNO 3for the deposition and stripping/AAS measurement, respectively.AcknowledgementThis work was supported by the application research(Project No. 451).REFERENCES1. PROUSEK, J.: Hazarded properties of the substances.Bratislava: STU, 2001.2. PRADOSH, R., ANUPAMA, S.: Current Science.1997, 82, 1.3. STN EN ISO 15586: Quality of the water: Determinationof trace elements by electrothermal atomicabsorption spectrometry. 2003.4. MENEMENLIOGLU, I., KORKMAZ, D., ATA-MAN, O. Y.: Spectrochimica <strong>Acta</strong>. 2007, Part B62 40–47.5. ANTHEMIDIS, A. N., KATZAMANIDOU, A.: 5thAegean Analytical Chemistry Days (AACD), Thessaloniki,2006.6. BEINROHR, E., MANOVA, A., DZUROV, J.: Preconcentrationof Cr(III) and total Cr in waters forflame AAS in a flow-through electrochemical/sorptioncell. Fresenius J Anal Chem, 1996, 355(5–6),p. 528–531.7. MOCAK, J, BOND, A. M., MITCHELL, S., SCOL-LARY, G.: A statistical overview of standard (IUPACand ACS) and new procedures for determining thelimits of detection and quantification: Application to<strong>vo</strong>ltammetric and stripping techniques (technical report).Pure and Appl. Chem, 1997, 69(2), p. 297–328.8. HENGWU CHEN, IAN D, BRINDLE, XIAO-CHUN LE: Prereduction of arsenic(v) to arsenic(iii),enhancement of the signal, and reduction of interferencesby l-cysteine in the determination of arsenicby hydride generation, Anal. Chemistry, 1992, 64(6),667–672
- Page 2 and 3: Acta FacultatisEcologiaeJournal of
- Page 4 and 5: OBSAH / CONTENTSISOL M., MICHALÍKO
- Page 6: 5ACTA FACULTATIS ECOLOGIAE, 16: Sup
- Page 12: 11ACTA FACULTATIS ECOLOGIAE, 16: Su
- Page 18 and 19: 17ACTA FACULTATIS ECOLOGIAE, 16: Su
- Page 20 and 21: 19are lower in ill patients compare
- Page 22: 21are considered as the most accura
- Page 25 and 26: 24- multimode cavities are usually
- Page 27 and 28: 26the load during its exposure to f
- Page 29 and 30: 28Tradescantia paludosa 02 test and
- Page 31 and 32: 30Tab. 5: Results of positive contr
- Page 34 and 35: 33ACTA FACULTATIS ECOLOGIAE, 16: Su
- Page 36 and 37: 35DISCUSSIONThe ionising radiation
- Page 38 and 39: 37ACTA FACULTATIS ECOLOGIAE, 16: Su
- Page 40 and 41: 39222Rn is produced by radioactive
- Page 42 and 43: 41180160140this reason we also pick
- Page 44: 435001450400350hKz0,8h [m]300250200
- Page 47: 46deposit is that stripped in off-l
- Page 51 and 52: 50MATERIAL AND METHODSChloroform (p
- Page 53 and 54: 52absorbance [a.u.]1,000,750,500,25
- Page 55 and 56: 54Tab. 1: Rrequirements determinati
- Page 57 and 58: 56Methods of VOC testing were set a
- Page 60 and 61: 59Tab. 6: ContinuedSamples withsurf
- Page 62 and 63: 61ACTA FACULTATIS ECOLOGIAE, 16: Su
- Page 64 and 65: 63One of the possible explanations
- Page 66 and 67: 65Ai - Ai-1 [Bq.m -3 ]86420-2-4-6-8
- Page 68 and 69: 67ACTA FACULTATIS ECOLOGIAE, 15: Su
- Page 70 and 71: 69BiodegradabilityThe great variety
- Page 72 and 73: 71degradation starts of late days,
- Page 74 and 75: 73Fig. 4 Treated (after 28 days of
- Page 76: 75parameters of the cutting process
- Page 80 and 81: 79Fraction: D (residual rest) prese
- Page 82: 81was not confirmed. Maximum of mer
- Page 85 and 86: 84Fig. 1 Schematic diagram of atomi
- Page 87 and 88: 86Alpha spectrometryAlpha spectrome
- Page 89 and 90: 8880007000y = 6622xR 2 = 0.939SIMS
- Page 92 and 93: 91ACTA FACULTATIS ECOLOGIAE, 16: Su
- Page 94 and 95: 93Gemer according to the German mod
- Page 96 and 97: 95Tab. 1 Results of the chemical an
- Page 98 and 99:
97Continuation of Tab. 2 Results of
- Page 100 and 101:
99Vlčia Dolina and from the reserv
- Page 102 and 103:
101ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 104 and 105:
103mg.dm -3mg.dm -35,004,003,002,00
- Page 106 and 107:
105year and the average value repre
- Page 108 and 109:
107ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 110 and 111:
109Sample site 1 Sample site 2 Samp
- Page 112 and 113:
111As for the sampling time (Fig. 5
- Page 114 and 115:
113ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 116 and 117:
115Typha latifolia, Carex sp., Scir
- Page 118 and 119:
117conditions for decomposition of
- Page 120 and 121:
119ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 122 and 123:
121from the background (derived fro
- Page 124 and 125:
12311. PETROVSKÝ, E., ELWOOD, B.:
- Page 126 and 127:
125ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 128 and 129:
1272.52.0Correlation coefficient 0,
- Page 130 and 131:
129ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 132 and 133:
131RESULTS AND DISCUSSIONTable 2 gi
- Page 134 and 135:
133ACTA FACULTATIS ECOLOGIAE, 16: S
- 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 142 and 143:
141ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 144 and 145:
143Fig. 2 The continuous monitoring
- Page 146 and 147:
145Indoor radon activity concentrat
- Page 148 and 149:
147ACTA FACULTATIS ECOLOGIAE, 16: S
- 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 158 and 159:
157decrease in the following order:
- Page 160 and 161:
159ACTA FACULTATIS ECOLOGIAE, 16: S
- Page 162 and 163:
161SPECIFIC EXAMPLES OFFACTORS THAT
- Page 164 and 165:
163ACTA FACULTATIS ECOLOGIAE, 16: S
- 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