Abstract:Chlorinated paraffins (CPs) are anthropogenic pollutants of growing environmental concern. These highly complex mixtures of thousands of homologs and congeners are usually applied as additives in lubricants or as flame retardants and plasticizers in polymers and paints. Recent studies indicated the presence of high amounts of CPs in the kitchen environment whose sources could not be unequivocally identified. One option was the use of CPs as or in lubricants of hinges. To test this hypothesis, we performed wipe… Show more
“…Scan time per ion was 62 ms for the developed GC/ECNI-MS-SIM screening method, whereas it was 28 ms for the comprehensive GC/ECNI-MS-SIM method. CP quantification was carried out analogously to the procedure of Sprengel and Vetter, 15 which was modified from Reth et al 25 isotope ratios as described previously by Sprengel and Vetter. 6 CP concentrations that gave a signal of the most abundant formed ion with a signal-to-noise ratio of 10 and 3, respectively, were considered as limits of quantification (LOQ) and limits of detection (LOD) of the single chain CP standards measured with the screening method.…”
Section: Instrumentationmentioning
confidence: 99%
“…Industrially produced since the 1930s, and used in different bulk applications (e.g., as lubricants, cutting fluids, plasticizers, and flame retardants 3,6–11 ), CPs are one of the industrial chemicals with the highest production volumes of currently more than 1 million tons per year 8,12–14 . Despite this versatility, SCCPs and MCCPs were shown to have detrimental environmental properties such as persistence, lipophilia, and—at least partly—(eco)toxicity 5,7,15 . Gradually, this group of anthropogenic pollutants has been detected worldwide in virtually all environmental matrices, as well as in food, indoor samples, and human milk 5,7,15–18 .…”
Section: Introductionmentioning
confidence: 99%
“…Typically, GC and high‐performance liquid chromatography (HPLC) in combination with low‐ or high‐resolution mass spectrometry (HRMS) are used in CP analysis (Table S1 in Sprengel and Vetter 15 ). 3 Among the various instrumental setups, GC coupled with electron capture negative ion mass spectrometry (GC/ECNI‐MS) in selected ion monitoring (SIM) mode is still the most commonly used method for SCCP and MCCP analysis (Table S1 in Sprengel and Vetter 15 ). 6 Although GC/ECNI‐MS (low resolution) instruments are comparatively affordable, the required efforts are high 15 .…”
Section: Introductionmentioning
confidence: 99%
“…still the most commonly used method for SCCP and MCCP analysis (Table S1 in Sprengel and Vetter 15 ). 6 Although GC/ECNI-MS (low resolution) instruments are comparatively affordable, the required efforts are high.…”
mentioning
confidence: 99%
“…Determined CP amounts were compared with an established comprehensive GC/ECNI-MS-SIM quantification method. 15 Comparative measurements included single chain-length CP standards, a technical CP product, and several edible oil samples with and without CPs.…”
Rationale
Chlorinated paraffins (CPs) are a group of anthropogenic pollutants that consist of complex mixtures of polychlorinated n‐alkanes of different chain lengths (~C10 to C30). Persistence, bioaccumulation, toxicity, and long‐range transport of short‐chain chlorinated paraffins (SCCPs, C10‐ to C13‐CPs) have prompted their classification as persistent organic pollutants (POPs) by the Stockholm Convention in 2017. Due to the varying chain lengths and chlorination degrees, quantification of SCCPs and medium‐chain chlorinated paraffins (MCCPs, C14‐ to C17) using gas chromatography coupled with electron capture negative ion mass spectrometry in selected ion monitoring mode (GC/ECNI‐MS‐SIM) is not only challenging but also very time consuming. In particular, up to eight GC runs per sample are required for the comprehensive GC/ECNI‐MS‐SIM quantification of SCCPs and MCCPs. These efforts are high especially if the samples do not contain CPs above the limit of detection (LOD), subsequently.
Methods
We developed a semi‐quantitative and sensitive method for the examination of SCCPs and MCCPs in one GC run. This GC/ECNI‐MS‐SIM screening method was based on the recording of Cl− (m/z 35 and 37), Cl2− (m/z 70 and 72), and HCl2− (m/z 71 and 73) isotope ions and evaluation of the ratios between them.
Results
Correctness of the results of the screening method was verified by analysis of edible oils with and without CPs, CP standards, as well as a technical CP mixture. Polychlorinated biphenyls (PCBs) and other polyhalogenated aromatic compounds, as well as brominated flame retardants, do not form all of the fragment ions analyzed by the screening method.
Conclusions
After the screening, only CP‐positive samples may need to be measured in detail. Measurement time will already be gained in the case of ~10% samples without CPs.
“…Scan time per ion was 62 ms for the developed GC/ECNI-MS-SIM screening method, whereas it was 28 ms for the comprehensive GC/ECNI-MS-SIM method. CP quantification was carried out analogously to the procedure of Sprengel and Vetter, 15 which was modified from Reth et al 25 isotope ratios as described previously by Sprengel and Vetter. 6 CP concentrations that gave a signal of the most abundant formed ion with a signal-to-noise ratio of 10 and 3, respectively, were considered as limits of quantification (LOQ) and limits of detection (LOD) of the single chain CP standards measured with the screening method.…”
Section: Instrumentationmentioning
confidence: 99%
“…Industrially produced since the 1930s, and used in different bulk applications (e.g., as lubricants, cutting fluids, plasticizers, and flame retardants 3,6–11 ), CPs are one of the industrial chemicals with the highest production volumes of currently more than 1 million tons per year 8,12–14 . Despite this versatility, SCCPs and MCCPs were shown to have detrimental environmental properties such as persistence, lipophilia, and—at least partly—(eco)toxicity 5,7,15 . Gradually, this group of anthropogenic pollutants has been detected worldwide in virtually all environmental matrices, as well as in food, indoor samples, and human milk 5,7,15–18 .…”
Section: Introductionmentioning
confidence: 99%
“…Typically, GC and high‐performance liquid chromatography (HPLC) in combination with low‐ or high‐resolution mass spectrometry (HRMS) are used in CP analysis (Table S1 in Sprengel and Vetter 15 ). 3 Among the various instrumental setups, GC coupled with electron capture negative ion mass spectrometry (GC/ECNI‐MS) in selected ion monitoring (SIM) mode is still the most commonly used method for SCCP and MCCP analysis (Table S1 in Sprengel and Vetter 15 ). 6 Although GC/ECNI‐MS (low resolution) instruments are comparatively affordable, the required efforts are high 15 .…”
Section: Introductionmentioning
confidence: 99%
“…still the most commonly used method for SCCP and MCCP analysis (Table S1 in Sprengel and Vetter 15 ). 6 Although GC/ECNI-MS (low resolution) instruments are comparatively affordable, the required efforts are high.…”
mentioning
confidence: 99%
“…Determined CP amounts were compared with an established comprehensive GC/ECNI-MS-SIM quantification method. 15 Comparative measurements included single chain-length CP standards, a technical CP product, and several edible oil samples with and without CPs.…”
Rationale
Chlorinated paraffins (CPs) are a group of anthropogenic pollutants that consist of complex mixtures of polychlorinated n‐alkanes of different chain lengths (~C10 to C30). Persistence, bioaccumulation, toxicity, and long‐range transport of short‐chain chlorinated paraffins (SCCPs, C10‐ to C13‐CPs) have prompted their classification as persistent organic pollutants (POPs) by the Stockholm Convention in 2017. Due to the varying chain lengths and chlorination degrees, quantification of SCCPs and medium‐chain chlorinated paraffins (MCCPs, C14‐ to C17) using gas chromatography coupled with electron capture negative ion mass spectrometry in selected ion monitoring mode (GC/ECNI‐MS‐SIM) is not only challenging but also very time consuming. In particular, up to eight GC runs per sample are required for the comprehensive GC/ECNI‐MS‐SIM quantification of SCCPs and MCCPs. These efforts are high especially if the samples do not contain CPs above the limit of detection (LOD), subsequently.
Methods
We developed a semi‐quantitative and sensitive method for the examination of SCCPs and MCCPs in one GC run. This GC/ECNI‐MS‐SIM screening method was based on the recording of Cl− (m/z 35 and 37), Cl2− (m/z 70 and 72), and HCl2− (m/z 71 and 73) isotope ions and evaluation of the ratios between them.
Results
Correctness of the results of the screening method was verified by analysis of edible oils with and without CPs, CP standards, as well as a technical CP mixture. Polychlorinated biphenyls (PCBs) and other polyhalogenated aromatic compounds, as well as brominated flame retardants, do not form all of the fragment ions analyzed by the screening method.
Conclusions
After the screening, only CP‐positive samples may need to be measured in detail. Measurement time will already be gained in the case of ~10% samples without CPs.
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