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. Author manuscript; available in PMC: 2016 Dec 5.
Published in final edited form as: Anal Bioanal Chem. 2015 Feb 5;407(11):2945–2954. doi: 10.1007/s00216-014-8441-0

Table 3.

Reference mass fraction values (μg/kg) for selected phenol metabolites in SRM 3672 organic contaminants in smokers’ urine and SRM 3673 organic contaminants in non-smokers’ urine

SRM 3672 SRM 3673
Bisphenol A(a,b) 3.05±0.16(c) 1.96±0.11(c)
2,5-Dichlorophenol(b) 1.77±0.06(d) 0.687±0.046(d)
Benzophenone-3(b) 191±5(d) 274±7(d)
Methyl Paraben(b) 113±2(d) 79.5±2.1(d)
Ethyl Paraben(b) 8.12±0.20(d) 10.3±0.3(d)
Propyl Paraben(b) 17.6±0.3(d) 21.6±0. 6(d)
Butyl Paraben(b) 11.1±0.2(d) 1.11±0.03(d)
Triclosan(b) 17.7±0.5(d) 6.27±0.32(d)
(a)

NIST analysis GC/MS

(b)

CDC analysis; data were converted from ng/mL to μg/kg using the density of the urine (1.019 g/mL)

(c)

The reference value is a weighted mean of average mass fractions, with one average from each of two analytical methods [30, 31]. The expanded uncertainty is the half-width of a symmetric 95 % parametric bootstrap confidence interval [32], which is consistent with the ISO Guide [33, 34]. The effective coverage factor, k, is 2

(d)

The reference mass fraction value is the mean of results obtained using one analytical technique. The expanded uncertainty, U, is calculated as U = kuc, where uc is one standard deviation of the analyte mean, and the coverage factor, k, is determined from the Student’s t-distribution corresponding to the associated degrees of freedom and a 95 % confidence level for each analyte. The effective coverage factor, k, is 2.20