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  • Gas chromatography-electron-capture detection of urinary methylhippuric acid isomers as biomarkers of environmental exposure to xylene.

Gas chromatography-electron-capture detection of urinary methylhippuric acid isomers as biomarkers of environmental exposure to xylene.

Journal of chromatography. B, Biomedical sciences and applications (1999-03-18)
M Buratti, O Pellegrino, C Valla, S Fustinoni, G Brambilla, A Colombi
RESUMEN

Methylhippuric acid isomers (MHAs), urinary metabolites of xylenes, were determined, after clean-up by C18-SPE and esterification with hexafluoroisopropanol and diisopropylcarbodiimide, by GC with ECD detection, on an SPB-35 capillary column (30 m, 0.32 mm I.D., 0.25 microm film thickness, beta = 320). S-benzyl-mercapturic acid was used for internal standardization. Chromatographic conditions were: oven temperature 162 degrees C, for 14.2 min; ramp by 30 degrees C/min to 190 degrees C, for 3.5 min; ramp by 30 degrees C/min to 250 degrees C, for 4 min; helium flow rate: 1.7 ml/min; detector and injector temperature: 300 degrees C. The sample (1 microl) was injected with a split injection technique (split ratio 5:1). MHA recovery was >95% in the 0.5-20 micromol/l range; the limit of detection was <0.25 micromol/l; day-to-day precision, at 2 micromol/l, was Cv<10%. Urinary MHAs were determined in subjects exposed to different low-level sources of xylenes: (a) tobacco smoking habit and (b) BTX urban air pollution (airborne xylene ranging from 0.1 to 3.7 micromol/m3). Study (a) showed a significant difference between urinary MHA median excretion values of nonsmokers and smokers (4.6 micromol/l vs. 8.1 micromol/l, p<0.001). Study (b) revealed a significant difference between indoor workers and outdoor workers (4.3 micromol/l vs. 6.9 micromol/l, p<0.001), and evidenced a relationship between MHAs (y, micromol/mmol creatinine) and airborne xylene (x, micromol/m3) (y = 0.085+0.34x; r = 0.82, p<0.001, n = 56). Proposed biomarkers could represent reliable tools to study very low-level exposure to aromatic hydrocarbons such as those observed in the urban pollution due to vehicular traffic or in indoor air quality evaluation.

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Supelco
SPB®-1, L × I.D. 30 m × 0.53 mm, df 3.00 μm
Supelco
SPB®-35, L × I.D. 30 m × 0.25 mm, df 0.25 μm