Component Description
The Family Smoking Prevention and Tobacco
Control Act of 2009 gave the Food and Drug Administration regulatory authority
over tobacco products. In Section 907(a), the Act states that the Secretary of
Health and Human Services shall establish tobacco product standards. These product standards shall
also include provisions for the testing of the
tobacco products. In order to determine the effectiveness of these product
standards, it is critical that surveillance systems be in place before the
standards are enacted to determine whether they impact exposure of people who
continue to use tobacco product. NHANES is an ideal source of human samples for
assessing smokers in multiple locations around the country. NHANES will provide
the most robust dataset possible for identifying changes in exposure of smokers
that should result from enactment of tobacco product standards.
We
anticipate that the results of this survey of tobacco exposure biomarkers will
be used by FDA, other government agencies, and research institutions. The
NHANES data will be used to determine the effectiveness of initial product
standards and direct whether further changes to product standards need to be
made.
Exposure to volatile organic compounds (VOCs) is
ubiquitous. Chronic exposure to high levels of some VOCs can lead to cancer and
neurocognitive dysfunction. Nearly 200 VOCs have been associated with adverse
health effects in occupational studies or laboratory studies, but have not been
monitored in general population groups. Metabolites of some VOCs can be
detected in urine following exposure events. Therefore, information on exposure
to these compounds, as measured by their metabolite concentrations in urine, is
essential to understand the levels of hazardous VOCs to which the general
population is exposed.
Eligible Sample
Urine collected from participants in NHANES 2005-2006 aged 12 years and older from a one-half subsample were eligible. Tests were conducted on residual urine samples.
Description of Laboratory Methodology
This
method is a quantitative procedure for the measurement of VOC metabolites in
human urine using ultra performance liquid chromatography coupled with electro
spray tandem mass spectrometry (UPLC-ESI-MS/MS) (Alwis et al., 2012).
Chromatographic separation is achieved using an Acquity UPLC® HSS T3 (Part no.
186003540, 1.8 mm x 2.1 mm x 150 mm, Waters, Inc.) column with 15 mM ammonium
acetate and acetonitrile as the mobile phases. The eluent from the column is
ionized using an electrospray interface to generate and transmit negative ions
into the mass spectrometer. Comparison of relative response factors (ratio of
native analyte to stable isotope labeled internal standard) with known standard
concentrations yields individual analyte concentrations.
Laboratory Quality Assurance and Monitoring
The analytical
measurements were conducted following strict quality control/quality assurance
CLIA guidelines. Along with the study samples, each analytical run included
high- and low-concentration quality control materials (QCs) and reagent blanks
to assure the accuracy and reliability of the data. The concentrations of the
high-concentration QCs and the low-concentration QCs, averaged to obtain one
measurement of high-concentration QC and low-concentration QC for each run, were
evaluated using standard statistical probability rules (Caudill et al. 2008).
Data Processing and Editing
The
data were reviewed. Incomplete data or improbable values were sent to the
performing laboratory for confirmation.
Analytic Notes
Bias Adjustments Applied to
VOC Metabolites in Urine Assay in NHANES 2005–2006 cycle (Surplus)
Several systematic biases
were discovered in measurements of certain urinary VOC metabolites in the 2005
– 2006 and 2011 – 2012 NHANES cycles. Upon further
investigation, in April 2022, the following adjustments have been applied to
the previously published data and included in the present dataset.
A. Adjustment to
correct calibrator errors of the CDC lab prepared calibration materials
During the
2005–2006 and 2011–2012 NHANES cycles, calibrators used for tests on several VOC
metabolites were prepared from a multi-analyte stock solution formulated from
neat materials prepared by the testing lab at CDC. Beginning with the NHANES
2015–2016 cycle, calibrators and the multi-analyte stock solution were prepared
externally. A systematic bias was observed between the cycles that used
in-house calibration materials and the cycle using externally prepared
calibration materials. The systematic nature of these biases permitted retrospective
adjustment through a statistical approach based on linear regression modeling
where adjusted measurements are predicted from unadjusted measurements using
suitable data. The “statistical recalibrations” implemented here have the
general form of a univariate linear regression equation (accounting for
dilution factors routinely used during measurement):
where exp[·] and ln(·)
are the natural exponential and natural logarithm functions, respectively.
Natural log-transformation of both the un-adjusted and adjusted measurements
moderated adverse influence on model fit from extreme measurements. The
estimated regression slope and intercept are m and b, respectively,
which are tabulated below for each analyte. The dilution factor was accounted
for only once for each analyte that underwent more than one statistical
recalibration (e.g., URXMB3). Statistical recalibration for the mass fraction
of salt (URXHP2, URXGAM) only required a regression slope (i.e., ).
The explanatory power of
the linear regressions was excellent (), and residuals exhibited distributions with good approximation
to normality, as well as stable variance over the observed range of
measurements. These favorable diagnostics demonstrate the efficacy of
statistical recalibration for the retrospective amelioration of systematic
bias.
Correction
for Change in Internal Standard
Isotopically labeled internal standards were not
commercially available for URXMB3 and URXHP2 during analysis of NHANES
2005–2006. Instead, the lab used surrogate internal standards. Isotopically labeled internal standards later
became available for purchase and were used in the NHANES 2011–2012 cycle. A
systematic bias between these two cycles was noted and confirmed to be due to
the internal standard change.
Analyte |
m used in correction |
b used in correction |
URXMB3 |
1.08034 |
0.73526 |
URXHP2 |
0.99437 |
0.21216 |
Correction
for Variation in Preparation of Neat Native Metabolites Standards
Validations of the externally prepared calibrators suggested that the calibrators previously prepared by the CDC testing lab were inaccurate due to special requirements for handling and preparing accurate solutions from neat materials, some of which are highly hygroscopic. Below is the list of analytes affected and the corresponding adjustment factors used in correction equation.
Analyte |
m used in correction |
b used in correction |
URXAMC |
0.99687 |
0.12843 |
URXCEM |
1.01462 |
-0.13642 |
URXDHB |
0.99654 |
0.04687 |
URXHEM |
1.00947 |
0.30195 |
URXHPM |
0.98949 |
-0.23802 |
URXMAD |
1.00736 |
-0.18993 |
URXTTC |
1.03057 |
-0.0746 |
URXMB3 |
0.97491 |
-0.43202 |
URX2DC |
1.00155 |
-0.32374 |
Correction
for Mass Fraction of Salt in Neat Compound Standard
During the 2005–2006 and 2011–2012 NHANES cycles,
calibrators were prepared from a multi-analyte stock solutions formulated from
neat materials in-house. Beginning with the NHANES 2015–2016 cycle, calibrators
and the multi-analyte stock solutions were prepared externally. A systematic
bias between the cycles that used in-house calibration materials and the cycle
using externally prepared calibration materials was observed for analytes
listed in the table below. Further validation confirmed that the large mass
fraction of salt in the neat materials was not accounted for during formulation
of in-house calibration materials. This discrepancy between the calculated
concentration of the calibrators and the actual concentration led to a
systematic bias in results for URXHP2 and URXGAM.
Analyte |
m used in correction |
URXHP2 |
0.5471199 |
URXGAM |
0.57755045 |
Correction
for Stereoisomerism in Urine Samples
URXMB3 occurs in human urine predominantly in the cis isomer, but quantitation in the
NHANES 2005–2006 and NHANES 2011–2012 cycles used standards containing the trans isomer. This discrepancy led to a
systematic bias in the URXMB3 results. Neat material that is purely cis isomer cannot be readily obtained, but
a predictive regression equation can account for these quantitative
differences.
Analyte |
m used in correction |
b used in correction |
URXMB3 |
0.97741 |
-0.18775 |
B. Adjustment to
correct calibrator errors of calibration materials prepared by an external
vendor
Correction of N-Acetyl-S-(3-Hydroxypropyl-1-Methyl)-L-Cysteine (URXPMM)
In the 2005-2006 and 2011-2016 NHANES
cycles, calibrators used to test N-Acetyl-S-(3-hydroxypropyl-1-methyl)-L-cysteine
(URXPMM) were externally prepared, by a vendor, from a multi-analyte
stock solution formulated from neat materials. In 2021, accuracy solutions from
a new vendor indicated a systematic bias. Validations conducted by the CDC
testing lab confirmed that the large mass fraction of salt in the neat
materials was not accounted for during formulation of the externally prepared
calibration materials from the previous vendor. This discrepancy between the
calculated concentration of the calibrators and the actual concentration led to
a systematic bias in results for URXPMM. An algebraic
correction factor of 0.565 were applied to the original URXPMM values and
released in the present file as below:
URXPMM = URXPMMOriginal × 0.565
Detection Limits
The detection limits were constant for the analytes in the data set. Two
variables are provided for each of these analytes. The variable named ending in
“LC” (ex., URDAAMLC) indicates whether the result was below the limit of
detection: the value “0” means that the result was at or above the limit of
detection, “1” indicates that the result was below the limit of detection. For
analytes with analytic results below the lower limit of detection (ex.,
URDAAMLC=1), an imputed fill value was placed in the analyte results field.
This value is the lower limit of detection divided by the square root of 2
(LLOD/sqrt [2]). The other variable prefixed URX (ex., URXAAM) provides the
analytic result for the analyte.
The lower limit of detection (LLOD, in µg/L) for urine VOC metabolites:
VARIABLE |
SAS LABEL |
LLOD |
URXAAM |
N-Acetyl-S-(2-carbamoylethyl)-L-cysteine |
2.2 |
URXAMC |
N-Acetyl-S-(N-methylcarbamoyl)-L-cysteine |
6.26 |
URXATC |
2-Aminothiazoline-4-carboxylic acid |
15 |
URXBMA |
N-Acetyl-S-(benzyl)-L-cysteine |
0.5 |
URXBPM |
N-Acetyl-S-(n-propyl)-L-cysteine |
1.2 |
URXCEM |
N-Acetyl-S-(2-carboxyethyl)-L-cysteine |
6.96 |
URXCYM |
N-Acetyl-S-(2-cyanoethyl)-L-cysteine |
0.5 |
URX1DC |
N-Acetyl-S-(1,2-dichlorovinyl)-L-cysteine |
12.6 |
URX2DC |
N-Acetyl-S-(2,2-dichlorovinyl)-L-cysteine |
4.7 |
URXDHB |
N-Acetyl-S-(3,4-dihydroxybutyl)-L-cysteine |
5.25 |
URXDPM |
N-Acetyl-S-(dimethylphenyl)-L-cysteine |
0.5 |
URXGAM |
N-Acetyl-S-(2-carbamoyl-2-hydroxyethyl)-L-cysteine |
9.4 |
URXHEM |
N-Acetyl-S-(2-hydroxyethyl)-L-cysteine |
0.791 |
URXHPM |
N-Acetyl-S-(3-hydroxypropyl)-L-cysteine |
13 |
URXHP2 |
N-Acetyl-S-(2-hydroxypropyl)-L-cysteine |
5.3 |
URXPMM |
N-Acetyl-S-(3-hydroxypropyl-1-methyl)-L-cysteine |
1.13 |
URXMAD |
Mandelic acid |
12 |
URX2MH |
2-Methylhippuric acid |
5 |
URX34M |
3-and 4-Methylhippuric acid |
8 |
URXMB1 |
N-Acetyl-S-(1-hydroxymethyl-2-propenyl)-L-cysteine |
0.7 |
URXMB2 |
N-Acetyl-S-(2-hydroxy-3-butenyl)-L-cysteine |
0.7 |
URXMB3 |
N-Acetyl-S-(4-hydroxy-2-butenyl)-L-cysteine |
0.6 |
URXPHE |
N-Acetyl-S-(phenyl-2-hydroxyethyl)-L-cysteine |
0.7 |
URXPHG |
Phenylglyoxylic acid |
12 |
URXPMA |
N-Acetyl-S-(phenyl)-L-cysteine |
0.6 |
URXTCV |
N-Acetyl-S-(trichlorovinyl)-L-cysteine |
3 |
URXTTC |
2-Thioxothiazolidine-4-carboxylic acid |
11.2 |