Determination of r-7,t-8,9,c-10-tetrahydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene in human urine by gas chromatography/negative ion chemical ionization/mass spectrometry
Cd. Simpson et al., Determination of r-7,t-8,9,c-10-tetrahydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene in human urine by gas chromatography/negative ion chemical ionization/mass spectrometry, CHEM RES T, 13(4), 2000, pp. 271-280
r-7,t-8,9,c-10-Tetrahydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene (trans-anti-B
aP-tetraol) is the major hydrolysis product of r-7,t-8-dihydroxy-t-9,10-epo
xy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BPDE), the principal ultimate ca
rcinogen of the environmental pollutant benzo[a]pyrene (BaP). As part of a
program to establish activation/detoxification profiles of urinary metaboli
tes of BaP in humans, we developed a method for quantifying trans-anti-BaP-
tetraol. Urine was collected from three groups of individuals exposed to Ba
P: psoriasis patients treated with a coal tar-containing ointment, steel wo
rkers, and smokers. [H-2(12)]-trans-anti-BaP-tetraol was added to the urine
as an internal standard. The urine was treated with beta-glucuronidase and
sulfatase, and then the BaP-tetraols were enriched by reverse-phase and ph
enylboronic acid solid-phase extraction. The resulting fraction was treated
with sodium hydride and methylmethane sulfonate to convert BaP-tetraols to
the corresponding tetramethyl ethers (BaP-TME). The mixture was purified b
y normal-phase HPLC and analyzed by gas chromatography/negative ion chemica
l ionization/mass spectrometry with selected ion monitoring. [(CH3)-C-13](4
)-trans-anti-BaP-TME was used as an external standard. Ions at mit 376, 380
, and 388 were monitored for quantitation of trans-anti-BaP-TME, [(CH3)-C-1
3](4)-trans-anti-BaP-TME, and [H-2(12)]-trans-anti-BaP-TME, respectively. T
he instrumental detection limit was approximately 1 fmol of trans-anti-BaP-
TME. trans-anti-BaP-tetraol las trans-anti-BaP-TME) was detected in 20 of 2
0 individuals receiving coal tar therapy (mean, 16 fmol/mL of urine), 13 of
13 exposed steel workers (mean, 4.1 fmol/mL of urine), and nine of 21 ciga
rette smokers (mean, 0.5 fmol/mL of urine). The means in these groups were
significantly different (P < 0.0001). The urine of steel workers was also a
nalyzed for cis-anti-BaP-tetraol and cys-syn-BaP-tetraol, but neither was f
ound. The results of this study provide a quantitative method for determina
tion of parts per trillion levels of trans-anti-BaP-tetraol in human urine.
Ultimately, this method can be employed as part of a phenotyping approach
for assessing BaP metabolites in human urine.