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Table 2:<br />

Regression functions and correlation coefficients of the studied<br />

pharmaceuticals<br />

Pharmaceutical Regression function R 2 Linearity<br />

range<br />

(ng/spot)<br />

LOD (ng/<br />

spot)<br />

LOQ<br />

(ng/<br />

spot)<br />

NOR A = 2.286 . 10 6 . + 930.8 0.994 0.75–7.5 0.5 0.75<br />

OTC A = 29.6400 . - 429.3 0.994 50–250 25 50<br />

TMP A = 6.3470 . - 6.821 0.997 75–300 50 75<br />

SDIAZ A = 38.8400 . + 1445.0 0.998 50–200 25 50<br />

SMETH A = 26.9500 . + 1496.0 0.999 50–200 25 50<br />

PGP A = 18.300 . + 1090.8 0.993 50–200 25 50<br />

SGUA A = 15.7500 . + 3265.0 0.996 150–550 100 150<br />

A-peak area.<br />

g-m<strong>as</strong>s concentration (ng/spot) (spot = 5 μL).<br />

Precision expressed in terms of RSD indicated high me<strong>as</strong>urement repeatability (Table<br />

3). In general, recoveries were dependent on the analyte concentration and values<br />

between 36.5% and 100.5% were obtained for all pharmaceuticals.<br />

Table 3:<br />

Recoveries and RSDs obtained for studied pharmaceuticals<br />

Pharmaceutical Recovery (%) RSD (n = 3)<br />

NOR 36.5 4.05<br />

OTC n.d. 2.86<br />

TMP 52.6 9.83<br />

SDIAZ 83.2 6.00<br />

SMETH 100.5 6.50<br />

PGP 44.7 3.12<br />

SGUA 78.5 4.88<br />

ND: not detected.<br />

According to validation parameters, it can be concluded that USE-TLC determination<br />

of veterinary antibiotics in soil is comparable with other commonly used extraction<br />

and chromatographic techniques, and convenient for determination of veterinary<br />

pollutants in soil (Thiele-Bruhn, 2003).<br />

ACKNOWLEDGEMENTS<br />

This work h<strong>as</strong> been supported by: EU project EMCO (INCO CT 2004-509188)<br />

- Reduction of environmental risks, posed by Emerging Contaminants, through<br />

advanced treatment of municipal and industrial w<strong>as</strong>tes and Croatian Ministry of<br />

Education, Science and Sport (Project No. 0125055).<br />

222

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