Perfluoroalkyl and polyfluoroalkyl substances (PFAS) are used in multiple commercial applications including surfactants, lubricants, paints, polishes, food packaging and fire-retarding foams. Certain PFAS are used in the manufacture of polymers used in many industrial and consumer products, including soil, stain, grease, and water resistant coatings on textiles and carpet; uses in the automotive, mechanical, aerospace, chemical, electrical, medical, and building/construction industries; personal care products; and non-stick coatings on cookware. Some PFASs are ubiquitous contaminants found in humans and animals worldwide.
Synthesis of PFAS employed electrochemical fluorination (ECF) or fluorotelomerization. ECF, used from the 1950s until the early 2000s, yielded branched and linear isomers. By contrast, fluorotelomerization produces almost exclusively linear compounds (Vyas, et al. 2007). The structural isomer patterns of perfluorooctanoate (PFOA) and perfluorooctane sulfonate (PFOS) in humans may be useful for understanding routes and sources of exposure (Benskin, et al. 2010). Therefore, concentrations of linear PFOA (n-PFOA), sum of branched isomers of PFOA (Sb-PFOA, branched PFOA isomers), linear PFOS (n-PFOS), and sum of perfluoromethylheptane sulfonate isomers (Sm-PFOS, monomethyl branched PFOS isomers) were measured in serum.
The calculated sum of isomers in the PFAS (formerly PFC) dataset for the 2015-2016 cycle is comparable to the total levels reported in previous cycles of NHANES.
Examined participants aged 12 years and older from a one-third sample were eligible.
Online solid phase extraction coupled to high performance liquid chromatography-turboionspray ionization-tandem mass spectrometry (online SPE-HPLC-TIS-MS/MS) is used for the quantitative detection of PFAS: 2-(N-methyl-perfluorooctane sulfonamido) acetate (Me-PFOSA-AcOH), perfluorohexane sulfonate (PFHxS), n-perfluorooctane sulfonate (n-PFOS), sum of perfluoromethylheptane sulfonate isomers (Sm-PFOS, monomethyl branched isomers of PFOS), n-perfluorooctanoate (n-PFOA), sum of branched perfluorooctanoate isomers (Sb-PFOA, branched PFOA isomers), perfluorononanoate (PFNA), perfluorodecanoate (PFDeA), perfluoroundecanoate (PFUA), and perfluorododecanoate (PFDoA)21. Briefly, after dilution with formic acid, one aliquot of 50 μL of serum is injected into a commercial column switching system allowing for concentration of the analytes on solid-phase extraction column. Separation of the analytes from each other and from other serum components is achieved with high-performance liquid chromatography. Detection and quantification are done using negative-ion TurboIonSpray ionization, a variant of electrospray ionization, tandem mass spectrometry. This method allows for rapid detection of these PFAS in human serum with limits of detection in the low parts per billion (ppb or ng/mL) range.
Refer to the Laboratory Method Files section for a detailed description of the laboratory methods used.
They were no changes to the lab method, lab equipment, or lab site for this component in the NHANES 2015-2016 cycle.
Perfluoroalkyl and Polyfluoroalkyl Substances (PFAS) Laboratory Procedure Manual (September 2018)
Serum specimens are processed, stored, and shipped to the Division of Laboratory Sciences, National Center for Environmental Health, Centers for Disease Control and Prevention, Atlanta, GA for analysis.
Detailed instructions on specimen collection and processing are discussed in the NHANES Laboratory Procedures Manual (LPM). Vials are stored under appropriate frozen (–20°C) conditions until they are shipped to National Center for Environmental Health for testing.
The NHANES quality assurance and quality control (QA/QC) protocols meet the 1988 Clinical Laboratory Improvement Act mandates. Detailed QA/QC instructions are discussed in the NHANES LPM.
Mobile Examination Centers (MECs)
Laboratory team performance is monitored using several techniques. NCHS and contract consultants use a structured competency assessment evaluation during visits to evaluate both the quality of the laboratory work and the quality-control procedures. Each laboratory staff member is observed for equipment operation, specimen collection and preparation; testing procedures and constructive feedback are given to each staff member. Formal retraining sessions are conducted annually to ensure that required skill levels were maintained.
Analytical Laboratories
NHANES uses several methods to monitor the quality of the analyses performed by the contract laboratories. In the MEC, these methods include performing blind split samples collected on “dry run” sessions. In addition, contract laboratories randomly perform repeat testing on 2% of all specimens.
NCHS developed and distributed a quality control protocol for all CDC and contract laboratories, which outlined the Westgard rules (Westgard, et al. 1981) used when running NHANES specimens. Progress reports containing any problems encountered during shipping or receipt of specimens, summary statistics for each control pool, QC graphs, instrument calibration, reagents, and any special considerations are submitted to NCHS quarterly. The reports are reviewed for trends or shifts in the data. The laboratories are required to explain any identified areas of concern.
All QC procedures recommended by the manufacturers were followed. Reported results for all assays meet the Division of Laboratory Science’s quality control and quality assurance performance criteria for accuracy and precision, similar to specifications outlined by Westgard rules (Caudill, et al. 2008).
The data were reviewed. Incomplete data or improbable values were sent to the performing laboratory for confirmation.
Refer to the 2015-2016 Laboratory Data Overview for general information on NHANES laboratory data.
Subsample weights
Serum PFAS were measured in a one-third subsample of persons 12 years and over. Special sample weights are required to analyze these data properly. Specific sample weights for this subsample are included in this data file and should be used when analyzing these data.
Demographic and Other Related Variables
The analysis of NHANES laboratory data must be conducted using the appropriate survey design and demographic variables. The NHANES 2015-2016 Demographics File contains demographic data, health indicators, and other related information collected during household interviews as well as the sample design variables. The recommended procedure for variance estimation requires use of stratum and PSU variables (SDMVSTRA and SDMVPSU, respectively) in the demographic data file.
The Fasting Questionnaire File includes auxiliary information, such as fasting status, the time of venipuncture, and the conditions precluding venipuncture.
This laboratory data file can be linked to the other NHANES data files using the unique survey participant identifier (i.e., SEQN).
Detection Limits
The detection limits were constant for all of the analytes in the data set. Two variables are provided for each of these analytes. The variable name ending in “L” (ex., LBDPFHSL) 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., LBDPFHSL=1), an imputed fill value was placed in the analyte results field. This value is the lower limit of detection divided by square root of 2 (LLOD/sqrt(2)). The other variable prefixed LBX (ex., LBXPFHS) provides the analytic result for that analyte.
The lower limit of detection (LLOD, in ng/mL) for each PFAS:
Variable Name |
SAS Label |
LLOD |
LBXPFDE |
Perfluorodecanoic acid (PFDeA) (ng/mL) |
0.10 |
LBXPFHS |
Perfluorohexane sulfonic acid (PFHxS) (ng/mL) |
0.10 |
LBXMPAH |
2-(N-methylperfluoroctanesulfonamido)acetic acid (Me-PFOSA-AcOH) (ng/mL) |
0.10 |
LBXPFNA |
Perfluorononanoic acid (PFNA) (ng/mL) |
0.10 |
LBXPFUA |
Perfluoroundecanoic acid (PFUA) (ng/mL) |
0.10 |
LBXPFDO |
Perfluorododecanoic acid (PFDoA) (ng/mL) |
0.10 |
LBXNFOA |
n-perfluorooctanoic acid (n-PFOA) (ng/mL) |
0.10 |
LBXBFOA |
Branch perfluorooctanoic acid isomers (Sb-PFOA) (ng/mL) |
0.10 |
LBXNFOS |
n-perfluorooctane sulfonic acid (n-PFOS) (ng/mL) |
0.10 |
LBXMFOS |
Perfluoromethylheptane sulfonic acid isomers (Sm-PFOS) (ng/mL) |
0.10 |
Please refer to the NHANES Analytic Guidelines and the on-line NHANES Tutorial for further details on the use of sample weights and other analytic issues.
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
16425.326175 to 874638.01159 | Range of Values | 2143 | 2143 | |
0 | No Lab Result | 27 | 2170 | |
. | Missing | 0 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 6.5 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 1318 | 1318 | |
1 | Below lower detection limit | 675 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 23.3 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 1962 | 1962 | |
1 | Below lower detection limit | 31 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 4.2 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 783 | 783 | |
1 | Below lower detection limit | 1210 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 11 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 1968 | 1968 | |
1 | Below lower detection limit | 25 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 4.2 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 751 | 751 | |
1 | Below lower detection limit | 1242 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 0.3 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 46 | 46 | |
1 | Below lower detection limit | 1947 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 20.4 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 1977 | 1977 | |
1 | Below lower detection limit | 16 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 0.5 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 40 | 40 | |
1 | Below lower detection limit | 1953 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 109.9 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 1982 | 1982 | |
1 | Below lower detection limit | 11 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0.07 to 19.2 | Range of Values | 1993 | 1993 | |
. | Missing | 177 | 2170 |
Code or Value | Value Description | Count | Cumulative | Skip to Item |
---|---|---|---|---|
0 | At or above the detection limit | 1970 | 1970 | |
1 | Below lower detection limit | 23 | 1993 | |
. | Missing | 177 | 2170 |