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Four polyvinyl chloride (PVC) matrix membrane electrodes responsive to 2 drugs affecting the urogenital system--oxybutynin hydrochloride (OX) and flavoxate hydrochloride (FX)--were developed, described, and characterized. A precipitation-based technique with tungstophosphate (TP) and ammonium reineckate (R) anions as electroactive materials in a PVC matrix with an OX cation was used for electrode 1 and 2 fabrication, respectively. Electrode 3 and 4 fabrication was based on use of the precipitation technique of FX cation with tetrakis (4-chlorophenyl) borate and R anions as electroactive materials. Fast and stable Nernstian responses in the range 1 x 10(-2)-1 x 10(-6) M for the 2 drugs over the pH range 5-8 revealed the performance characteristics of these electrodes, which were evaluated according to International Union of Pure and Applied Chemistry recommendations. The method was applied to FX and OX in their pharmaceutical formulations and in human plasma samples. The 4 proposed sensors were found to be specific for the drugs in the presence of up to 60% of their degradation products. Validation of the method according to the quality assurance standards showed suitability of the proposed electrodes for use in the quality control assessment of these drugs. The recoveries for determination of the drugs by the 4 proposed selective electrodes were 99.5 +/- 0.5, 100.0 +/- 0.4, 99.9 +/- 0.4, and 100.1 +/- 0.4% for sensors 1-4, respectively. Statistical comparison between the results obtained by this method and the official method of the drugs was done, and no significant difference found.

A purge-and-trap gas chromatographic (PT-GC) method for determining styrene concentrations in urine and blood samples has been used in the biological monitoring of workers exposed to styrene and acetone. Blood and urine samples were collected from 34 individuals exposed to both solvents at the end of a 4-h shift and measured for styrene in urine (Su), blood (Sb), and the two major urinary metabolites, mandelic acid (MA) and phenylglyoxylic acid (PGA). A second urine sample was taken at the beginning of the next shift. Environmental exposure was measured using passive personal monitoring and GC. Urinary excretion of MA and PGA was measured by high-performance liquid chromatography. The average exposures to styrene and acetone were 70.5 mg/m3 and 370.5 mg/m3, respectively. In end-of-shift samples there was a significant correlation between concentrations of Su and Sb and the metabolites PGA, MA (r = 0.714 and 0.788, p < 0.001 for Su and r = 0.644 and 0.566, p < 0.005 for Sb). A high correlation between Sb and Su (r = 0.732, p < 0.001) also existed. Poor correlations were found between Su and metabolites in samples collected at the beginning of the next shift (r = 0.491 and 0.474 for PGA and MA, respectively, p < 0.05). There was a better correlation between the biological parameters at the end of the shift and the environmental styrene (r = 0.841 for PGA, r = 0.834 for MA, r = 0.788 for Su, and r = 0.698 for Sb; p < 0.001) compared with those at the start of the shift (r = 0.81 for PGA, 0.675 for MA, and 0.650 for Su; p < 0.001). We found that the concentration of excreted metabolites decreased significantly when environmental concentrations of acetone increased (p < 0.05), particularly at the end of the shift. Although the best correlation with environmental styrene was obtained with the sum of PGA and MA at the end of the shift (r = 0.862, p < 0.001), urine and blood styrene were shown to be more useful biological monitoring indicators because their concentrations were not affected by acetone co-exposure.