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2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

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Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />

Table III<br />

Comparison of efficiency of extraction by Pn-ICP-OES to<br />

XRF analysis<br />

Element Efficiency [%]<br />

Cr 63<br />

ni 82<br />

Cu 80<br />

Zn 102<br />

Pb 96<br />

metals by Pn-ICP-OES. The results as a sum of the five<br />

extraction steps were compared with those obtained after<br />

total decomposition and by XRF spectrometry. Efficiency<br />

of soil extracts to pressed pellets together with correlation<br />

coefficients are presented in Table III. The best efficienty of<br />

extraction can be observed for lead and zinc. Efficiency of<br />

extraction depends on the binding to minerals with different<br />

solubility. Low efficiency of chromium can be explained by<br />

binding to poorly soluble chromspinels and chromite 12,13 .<br />

The soil samples were analysed to evaluate the possibility<br />

of quantitative elemental analysis by laser ablation. The<br />

results for LA-ICP-MS were compared with the results of<br />

XRF as a method representing another type of direct analysis<br />

and with the results of solution analysis by ICP-OES as an<br />

ordinary method. In the case of Cr, slightly lower concentration<br />

values were yielded for the total decomposition using<br />

Pn-ICP-OES than for both direct analysis methods, which<br />

can be caused by the incomplete decomposition of Cr in acids<br />

(Fig. <strong>2.</strong>).<br />

Fig. <strong>2.</strong> Comparison of LA-ICP-MS and PN-ICP-OES after total<br />

decomposition results for Cr as a barely leachable element<br />

The calibration was performed using spiked sample pellets.<br />

The soil with a low content of elements of interest was<br />

spiked with seven concentration levels to obtain a calibrated<br />

range from 24 to 965 mg kg –1 . The calibration curves were<br />

fitted by a computer program WinStat. All calibration plots<br />

were linear over the whole concentration range. Intercepts of<br />

the regression lines were tested by t-test and were statistically<br />

insignificant (t a < t 0.05;n-2 ) for all studied elements. Correla-<br />

s315<br />

Table IV<br />

Comparison of CRM GBW07407 soil analysis results by<br />

LA-ICP-MS and certified values; the uncertainty intervals<br />

are calculated on a 95 % confidence level<br />

Method [mg kg–1 ] LA-ICP-MS Certified value<br />

Cr 432 ± 28 410 ± 23<br />

ni 269 ± 27 276 ± 15<br />

Cu 84 ± 8 97 ± 6<br />

Zn 139 ± 15 142 ± 11<br />

Pb 15 ± 3 14 ± 3<br />

tion coefficient r values were in the range of 0.997–0.999.<br />

Calibration line for copper with scandium as internal standard<br />

is presented in Fig. 3.<br />

Repeatability of ablation was described as RSD % which<br />

was calculated from three measurements of ablation signal on<br />

the different locations of each pellet. The RSD values did not<br />

exceed 8%.<br />

The accuracy of the method was confirmed by analysis<br />

of three CRM soils. Results of CRM GBW 7407 by LA-ICP-<br />

MS and certified values are given in Table IV.<br />

Fig. 3. Calibration graph for Cu with internal standardization<br />

by Sc<br />

Conclusions<br />

Monitoring of the heavy metals in agricultural soils is gaining<br />

the importance because these elements can be accumulated<br />

by plants and thus enter the food chain. To obtain total<br />

elemental content of Cr, ni, Cu, Zn, Pb the decomposition<br />

with HF and HClO 4 by ICP-OES was used. The sequential<br />

extraction procedure providing more information than total<br />

concentration determination was used to study bioavailability<br />

of metals. Methods of total decomposition are very lengthy<br />

and sometimes even not fully efficient therefore direct<br />

methods are more convenient in such a case. XRF analysis<br />

of soil pellets prepared with a wax binder and LA-ICP-MS<br />

of perfectly homogenized pellets using sol-gel method represented<br />

the direct methods.<br />

The results of direct methods were compared with those<br />

obtained by Pn-ICP-OES. A satisfactory agreement was

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