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13 c bde 209

Manufactured by Wellington Laboratories
Sourced in Canada
About the product

13 C-BDE-209 is a chemical reference standard used for analytical purposes. It is a 13C-labeled analogue of the polybrominated diphenyl ether (PBDE) congener BDE-209. This product is intended for use in analytical procedures, such as method development, validation, and quantification of BDE-209 in environmental or biological samples.

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9 protocols using «13 c bde 209»

1

BDE Congener Quantification in Liver

The concentration of 29 BDE congeners in liver samples collected at sacrifice were determined using gas chromatography/mass spectrometry operated in electron capture negative ionization mode (ECNI) as previously described94 (link). Samples were analyzed for nine congeners that comprise the DE-71 lot used as described17 (link) (BDE-17, 28/33, -47, -85/155, -99, -100, -138, 153, -154) as well as -25, -30, -49, -66, -71, -75, -116, -119, -156, -181, -183, -190, -191, -200/203, -205, -206, -209 that are commonly monitored in the environment. There are only 6 congeners that make up the great majority (96%) of the DE-71 mixture used here: BDE-99 > -47 > -100 > -153 > -154 > -85 that range from 45.0 to 2.54% w/w17 (link). Similarly, 5 of these are the most prevalent BDE congeners found in human tissues: BDE-28, -47, -99, -100, and -15395 (link) (Center for Disease Control and Prevention, NHANES, 2015). Prior to extraction, two internal standards were spiked into the homogenized tissue, including a monofluorinated BDE congener (F-BDE-69; Accustandard Inc.) and isotopically labeled BDE-209 (13C BDE-209; Wellington Laboratories). BDE congeners were extracted from liver tissues (approximately 1 g) using sonication and an aliquot of the extract was used for gravimetric analysis of lipid content. The remaining extract was purified using a Florisil solid phase extraction cartridge. Extracts were spiked with a third standard, isotopically labeled chlorinated diphenyl ether (13C CDE-141; Wellington Laboratories) to measure recovery of the internal standards and then analyzed via gas chromatography mass/ spectrometry using ECNI with methane as a reagent gas as previously described. BDE concentrations are expressed as ng/g lipid weight. The method detection limit (MDL) was calculated using 3 times the standard deviation of the laboratory blanks and was equivalent to 0.5 ng/g lw. Recoveries of F-BDE-69 averaged 90.9% ± 6.9% while 13C BDE 209 averaged 106% ± 19%.
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2

Chlorinated Paraffin Biotransformation Assessment

2020
Commercial SCCP mixtures (Cl degree: 55.5%), MCCP mixtures (Cl degree: 52%), and LCCP mixtures (Cl degree: 49%) were purchased from Dr. Ehrenstorfer (Augsburg, Germany). 13 C-BDE 209 was purchased from Wellington Laboratories Inc (Guelph, ON, Canada). Pooled human liver microsomes (HLM), pooled human liver cytosol (HLCYT), 2,6-uridinediphosphate glucuronic acid (UDPGA), alamethicin (neat, purity > 99%), 3'-phosphoadenosine-5'-phosphosulfate (PAPS; purity > 60%) lithium salt hydrate, nicotinamide adenine dinucleotide phosphate (NADPH; purity > 99%), and dimethyl sulfoxide (DMSO) were purchased from Sigma-Aldrich (Castle Hill, NSW, Australia). Ultrapure water was obtained from a Milli-Q system (Merck Millipore, MA, USA). Gas chromatography grade acetonitrile (ACN) was purchased from Merck (Darmstadt, Germany).
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3

Chlorinated Organic Compounds: Extraction and Characterization

2019
Commercial SCCP mixtures (Cl degrees: 51.5%, 55.5% and 63%), MCCP mixtures (Cl degrees: 42%, 52%, and 57%), and LCCP mixtures (Cl degrees: 36% and 49%) were purchased from Dr. Ehrenstorfer (Auguburg, Germany). 13 C-BDE 209 was purchased from Wellington Laboratories Inc. (Guelph, ON, Canada). Gas chromatography grade dichloromethane (DCM), n-hexane, acetone and acetonitrile (ACN) were purchased from Merck (Darmstadt, Germany). Kimwipes were purchased from Kimtech Science (Roswell, GA). Silica gel (40-60 μm), sodium sulphate and sulphuric acid were purchased from Sigma Aldrich (Castle Hill, NSW, Australia) Silica gel was baked at 140 °C for 24 h before activation by addition of 40% sulphuric acid (98%) on a w/w basis.
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4

Quantitative Analysis of Persistent Organic Pollutants

2017
BDE-77, BDE-128, 13 C-BTBPE, 13 C-BDE-209 and PCB-129 purchased from Wellington Laboratories Inc. were used as internal standards (IS). All solvents used (acetone, n-hexane, iso-octane (2, 2, and DCM (dichloromethane)) were HPLC grade.
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5

Determination of Brominated Flame Retardants

2017
Solvents used were all of HPLC analytical grade (Fisher Scientific, Loughborough, UK).
Standards of BDEs 28, 47, 99, 100, 153, 154, 183 and 209 , α, β-DBE-DBCH, BTBPE, DBDPE, EH-TBB, BEH-TEBP and labelled internal standards (IS) 13C-BDE 209, 13C-BTBPE, 13C-BEH-TEBP and 13C-HBCDD were purchased from Wellington Laboratories (Guelph, ON, Canada). BDEs 77 and 128 (IS) were obtained from Accustandard (New Haven, CT, USA).
TBBPA-BDBPE was purchased from Dr. Ehrenstorfer (Essex, UK). HBCDDs were obtained from Sigma-Aldrich Company Ltd. (Dorset, UK).
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