Biomonitoring: Polybrominated Diphenyl Ethers and Polybrominated Biphenyls Using Capillary GC with Electron-Capture Negative
Ion Mass Selective
Polybrominated diphenyl ethers (PBDEs) have emerged as a significant class of persistent organic pollutants (POPs). These
POPs join the organochlorine pesticides (OCs) and polychlorinated biphenyl (PCB) and polybrominated (PBB) biphenyl congeners
as environmentally significant POPs that must be biomonitored continuously. Potential threats to human and animal health include
developmental neurotoxicity, endocrine disruption, peripheral nervous system damage and cancer (1,2). Morland and colleagues
(3) cite two reported adverse health outcomes in laboratory animals dosed with high levels of PBDEs to include neurologic
deficiencies and endocrine disruption . Sjödin and colleagues (4) at the Centers for Disease Control and Prevention (CDC)
report an increase in the concentration of PBDEs measured in 40 human serum pools collected in the southeastern United States
from 1985 through 2002 and in Seattle, Washington, from 1999 through 2002. In contrast, 2,2',4,4',5,5'-hexabromobiphenyl (BB-153),
the principal PBB congener from the original Firemaster (Formerly the Michigan Chemical Corporation, St. Louis, Missouri)
fire retardant product that inadvertently contaminated livestock and entered the human food chain in Michigan in 1973 (5,6)
as well as 2,2',4,4',5,5'-hexachlorobiphenyl (CB-153) also were measured and found to be decreasing over this time period.
Sjödin and colleagues (7) at the CDC recently reported serum concentration levels of 10 BDE congeners and BB-153 in representative
sampling of U.S. residents in 2003 and 2004. Out of 2062 serum samples, almost all serum samples contained detectable levels
of BDE-47.
Covaci and colleagues (8) recently reviewed the literature on the isolation and recovery of PBDEs from both environmental
and human samples. They stated that when it is impossible to use 13C-labeled PBDEs as internal standards, PBDE congeners that are not present in technical mixtures or environmental samples
are suitable as internal standards. Fluorinated derivatives (F-PBDEs) also make suitable internal standards. Many laboratories
cannot afford high resolution mass spectrometers that would allow use of 13C-labeled PBDEs to be able to quantitate PBDEs by isotope dilution. Korytár and colleagues (9) established elution orders
for seven different GC stationary phases and concluded that one of the columns resulted in the least number of coelutions.
For biomonitoring purposes, only a small number of PBDE congeners have been found in environmental and biological samples
in contrast to PCBs. The following congeners are suggested as targeted analytes for biomonitoring: BDEs 28 (2,4,4'-tribromo-diphenylether),
47 (2,2',4,4'-tetrabromo-diphenylether), 99 (2,2',4,4'5-pentabromo-diphenylether), 100 (2,2',4,4',6-pentabromo-diphenylether),
153 (2,2',4,4'5,6'-hexabromo-diphenylether), 154 (2,2',4,4'5,6'-hexabromodiphenylether) and 183 (2,2',3,4,4',4',6-heptabromo-diphenylether).
Björklund and colleagues (10) in Sweden investigated the influence of several injection techniques while testing 10 different
wall-coated open tubular (WCOT) columns including the use of retention gaps. They conclude from their studies that the programmed
temperature vaporizing (PTV) injector operated in temperature programmed pulsed pressure injection mode is recommended for
PBDEs. In this article, we demonstrate how a PTV injector was incorporated along with a 30-m WCOT column in a capillary GC–MS system
utilizing electron capture negative ion with selected ion monitoring (ECNI-MSD) detection using methane as buffer or reagent
gas to achieve sufficient chromatographic resolution of the most commonly detected PBDE congeners. Baseline chromatographic
resolution of BB-153 from BDE-154 without resorting to a longer WCOT column was demonstrated. We show that the incorporation
of an internal standard mode of instrument calibration led to a significant cost reduction to quantitate PBDEs and PBBs in
sample extracts from biological matrices. To assess instrument sensitivity, we then studied the calibration data generated
over a six-month period. Using an ordinary (nonweighted) least squares regression approach, the author established decision
levels, decision limits, and instrument detection limits (IDLs) for each congener based upon calibration statistics using
computer programs published elsewhere (11). Our objective was to achieve the lowest IDLs for nine BDE congeners and two BB
congeners and, thus, to add value to an existing biomonitoring program in public health for the state of Michigan.