Abstract:To survey the conformity and quality of the results between laboratories for short-chain chlorinated paraffins (SCCPs) determination, we reviewed current and novel analytical methods and organized four worldwide laboratory exercises between 2011 and 2017. Participants were requested to analyse test solutions and extracts of various matrices with their method of choice. Thirty-three laboratories participated (9e22 per round), of which 55e81% were able to submit data. Large differences in results between laborat… Show more
“…This is comparable with the average CP levels ( n = 3) observed in our study, 7.1 ± 0.2 μg/g ( R 2 = 0.93) for the SCCPs, 10 ± 0.2 μg/g ( R 2 = 0.71) for the MCCPs. Especially considering that the between lab coefficient of variation (CV) of the laboratory exercises organized between 2011 and 2017 were 23–137% 23 and that two different analysis techniques are used, the GC–MS operated in electron capture negative ion (ECNI) chemical ionization mode by Shang et al 22 and the APCI-qTOF-MS method in our study. In addition to CPs various other chlorinated compounds have been detected in the NIST SRM2585 dust sample.…”
Chlorinated
paraffins (CPs) are used in various products to improve
their physicochemical characteristics. Due to recycling, CPs may end
up in “new” recycled products. In this study we investigated
CPs present in end-of-life car tires that are recycled to rubber granulates
used on artificial soccer fields, and playground tiles. The ∑CP(C10-C30) concentrations ranged from 1.5 to 67 μg/g
in car tires, 13–67 μg/g in rubber granulates, and 16–74
μg/g in playground tiles. MCCPs were the dominant CP group with
an average contribution of 72%. LCCPs up to C30, were detected
for the first time in car tires, rubber granulates, and playground
tiles. The CPs application in tires is unclear, the low CP concentrations
found in this study (<0.007%) could possibly indicate contamination
during the manufacturing process. The presence of CPs in the granulates
and tiles, in addition to the multiple chemicals already detected,
emphasizes the need to further investigate the migration and leaching
behavior, in order to assess potential risks of CPs for humans and
the environment. The presence of CPs in car tires may be another source
of CPs for the environment. The CP volume brought into the environment
by tire wear particles (TWP) from car tires in the European Union,
is estimated at 2.0–89 tons annually.
“…This is comparable with the average CP levels ( n = 3) observed in our study, 7.1 ± 0.2 μg/g ( R 2 = 0.93) for the SCCPs, 10 ± 0.2 μg/g ( R 2 = 0.71) for the MCCPs. Especially considering that the between lab coefficient of variation (CV) of the laboratory exercises organized between 2011 and 2017 were 23–137% 23 and that two different analysis techniques are used, the GC–MS operated in electron capture negative ion (ECNI) chemical ionization mode by Shang et al 22 and the APCI-qTOF-MS method in our study. In addition to CPs various other chlorinated compounds have been detected in the NIST SRM2585 dust sample.…”
Chlorinated
paraffins (CPs) are used in various products to improve
their physicochemical characteristics. Due to recycling, CPs may end
up in “new” recycled products. In this study we investigated
CPs present in end-of-life car tires that are recycled to rubber granulates
used on artificial soccer fields, and playground tiles. The ∑CP(C10-C30) concentrations ranged from 1.5 to 67 μg/g
in car tires, 13–67 μg/g in rubber granulates, and 16–74
μg/g in playground tiles. MCCPs were the dominant CP group with
an average contribution of 72%. LCCPs up to C30, were detected
for the first time in car tires, rubber granulates, and playground
tiles. The CPs application in tires is unclear, the low CP concentrations
found in this study (<0.007%) could possibly indicate contamination
during the manufacturing process. The presence of CPs in the granulates
and tiles, in addition to the multiple chemicals already detected,
emphasizes the need to further investigate the migration and leaching
behavior, in order to assess potential risks of CPs for humans and
the environment. The presence of CPs in car tires may be another source
of CPs for the environment. The CP volume brought into the environment
by tire wear particles (TWP) from car tires in the European Union,
is estimated at 2.0–89 tons annually.
“…This is also very reasonable if we consider the results from the available interlaboraty studies with SCCPs. [83][84][85] Tomy et al 83 found differences between the assigned values and the reported concentrations from -30% to 310%. The latest interlaboratory study of van Mourik et al 85 reported differences of up to 54%.…”
Section: General Remarksmentioning
confidence: 97%
“…[83][84][85] Tomy et al 83 found differences between the assigned values and the reported concentrations from -30% to 310%. The latest interlaboratory study of van Mourik et al 85 reported differences of up to 54%. Therefore, we will take a more general approach and interpret ranges of the measured concentrations rather than single values.…”
Chlorinated paraffins are industrial chemicals that can be subdivided into short-chain (SCCP), medium-chain (MCCP), and long-chain (LCCP) chlorinated paraffins. The global production volumes of MCCPs are nowadays suspected to be much higher than those of S- and LCCPs, and the few available studies on the environmental occurrence of chlorinated paraffins report often higher MCCP concentrations than S- or LCCP concentrations in the environment. The present review focuses, therefore, on MCCPs specifically and provides a literature overview and a data analysis of the production volumes, PBT properties (persistence, bioaccumulation potential, and toxicity), and the worldwide measured concentrations of MCCP in environmental samples, biota, and humans. Furthermore, we include our own measurements of technical CP formulations from China, the major global producing country, to estimate the global production amounts of MCCPs. The key findings from this review are that (1) MCCPs are toxic to the aquatic environment, and the available data suggest that they are also persistent; (2) available time trends for MCCPs in soil, biota, and most of the sediment cores show increasing time trends over the last years to decades; and (3) MCCP concentrations in sediment close to local sources exceed toxicity thresholds (i.e., the PNEC). Our study shows that overall, MCCPs are of growing concern, and regulatory actions should be considered seriously.
“…This requires reliable analytical methods and agreement in results between laboratories. However, recent proficiency tests show large differences in reported SCCP levels for the same samples (naturally contaminated) between laboratories (up to 137% coefficient of variation) [6] . This is mainly due to their challenging determination, as described extensively elsewhere [7] .…”
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