Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry

The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by worke...
Ausführliche Beschreibung

Gespeichert in:

Autor*in:	Schettgen, Thomas [verfasserIn] Esser, André [verfasserIn] Kraus, Thomas [verfasserIn] Ziegler, Patrick [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2021

Schlagwörter:	Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants

Übergeordnetes Werk:	Enthalten in: Chemosphere - Amsterdam [u.a.] : Elsevier Science, 1972, 291
Übergeordnetes Werk:	volume:291

DOI / URN:	10.1016/j.chemosphere.2021.132722

Katalog-ID:	ELV00728182X

Internformat


LEADER	01000caa a22002652 4500
001	ELV00728182X
003	DE-627
005	20230524123222.0
007	cr uuu---uuuuu
008	230506s2021 xx \|\|\|\|\|o 00\| \|\|eng c
024	7		\|a 10.1016/j.chemosphere.2021.132722 \|2 doi
035			\|a (DE-627)ELV00728182X
035			\|a (ELSEVIER)S0045-6535(21)03194-5
040			\|a DE-627 \|b ger \|c DE-627 \|e rda
041			\|a eng
082	0	4	\|a 333.7 \|q DE-600
084			\|a 43.00 \|2 bkl
100	1		\|a Schettgen, Thomas \|e verfasserin \|0 (orcid)0000-0003-1256-1713 \|4 aut
245	1	0	\|a Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry
264		1	\|c 2021
336			\|a nicht spezifiziert \|b zzz \|2 rdacontent
337			\|a Computermedien \|b c \|2 rdamedia
338			\|a Online-Ressource \|b cr \|2 rdacarrier
520			\|a The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry.
650		4	\|a Biological monitoring
650		4	\|a PCB
650		4	\|a Exposure assessment
650		4	\|a Mixtures
650		4	\|a Persistent organic pollutants
700	1		\|a Esser, André \|e verfasserin \|4 aut
700	1		\|a Kraus, Thomas \|e verfasserin \|4 aut
700	1		\|a Ziegler, Patrick \|e verfasserin \|4 aut
773	0	8	\|i Enthalten in \|t Chemosphere \|d Amsterdam [u.a.] : Elsevier Science, 1972 \|g 291 \|h Online-Ressource \|w (DE-627)306354217 \|w (DE-600)1496851-4 \|w (DE-576)081952961 \|x 1879-1298 \|7 nnns
773	1	8	\|g volume:291
912			\|a GBV_USEFLAG_U
912			\|a SYSFLAG_U
912			\|a GBV_ELV
912			\|a SSG-OLC-PHA
912			\|a SSG-OPC-GGO
912			\|a GBV_ILN_20
912			\|a GBV_ILN_22
912			\|a GBV_ILN_23
912			\|a GBV_ILN_24
912			\|a GBV_ILN_31
912			\|a GBV_ILN_32
912			\|a GBV_ILN_40
912			\|a GBV_ILN_60
912			\|a GBV_ILN_62
912			\|a GBV_ILN_63
912			\|a GBV_ILN_69
912			\|a GBV_ILN_70
912			\|a GBV_ILN_73
912			\|a GBV_ILN_74
912			\|a GBV_ILN_90
912			\|a GBV_ILN_95
912			\|a GBV_ILN_100
912			\|a GBV_ILN_105
912			\|a GBV_ILN_110
912			\|a GBV_ILN_151
912			\|a GBV_ILN_224
912			\|a GBV_ILN_370
912			\|a GBV_ILN_602
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2027
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2038
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2056
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2065
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2111
912			\|a GBV_ILN_2112
912			\|a GBV_ILN_2113
912			\|a GBV_ILN_2118
912			\|a GBV_ILN_2122
912			\|a GBV_ILN_2129
912			\|a GBV_ILN_2143
912			\|a GBV_ILN_2147
912			\|a GBV_ILN_2148
912			\|a GBV_ILN_2152
912			\|a GBV_ILN_2153
912			\|a GBV_ILN_2190
912			\|a GBV_ILN_2336
912			\|a GBV_ILN_2507
912			\|a GBV_ILN_2522
912			\|a GBV_ILN_4035
912			\|a GBV_ILN_4037
912			\|a GBV_ILN_4112
912			\|a GBV_ILN_4125
912			\|a GBV_ILN_4126
912			\|a GBV_ILN_4242
912			\|a GBV_ILN_4251
912			\|a GBV_ILN_4305
912			\|a GBV_ILN_4313
912			\|a GBV_ILN_4323
912			\|a GBV_ILN_4324
912			\|a GBV_ILN_4325
912			\|a GBV_ILN_4326
912			\|a GBV_ILN_4333
912			\|a GBV_ILN_4334
912			\|a GBV_ILN_4335
912			\|a GBV_ILN_4338
912			\|a GBV_ILN_4393
936	b	k	\|a 43.00 \|j Umweltforschung \|j Umweltschutz: Allgemeines
951			\|a AR
952			\|d 291

Indexfelder

author_variant	t s ts a e ae t k tk p z pz
matchkey_str	article:18791298:2021----::lsaeesfnnetoalpouennrcoplclrntdihnlccneesnokr
hierarchy_sort_str	2021
bklnumber	43.00
publishDate	2021
allfields	10.1016/j.chemosphere.2021.132722 doi (DE-627)ELV00728182X (ELSEVIER)S0045-6535(21)03194-5 DE-627 ger DE-627 rda eng 333.7 DE-600 43.00 bkl Schettgen, Thomas verfasserin (orcid)0000-0003-1256-1713 aut Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry 2021 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry. Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants Esser, André verfasserin aut Kraus, Thomas verfasserin aut Ziegler, Patrick verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 291 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:291 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 43.00 Umweltforschung Umweltschutz: Allgemeines AR 291
spelling	10.1016/j.chemosphere.2021.132722 doi (DE-627)ELV00728182X (ELSEVIER)S0045-6535(21)03194-5 DE-627 ger DE-627 rda eng 333.7 DE-600 43.00 bkl Schettgen, Thomas verfasserin (orcid)0000-0003-1256-1713 aut Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry 2021 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry. Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants Esser, André verfasserin aut Kraus, Thomas verfasserin aut Ziegler, Patrick verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 291 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:291 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 43.00 Umweltforschung Umweltschutz: Allgemeines AR 291
allfields_unstemmed	10.1016/j.chemosphere.2021.132722 doi (DE-627)ELV00728182X (ELSEVIER)S0045-6535(21)03194-5 DE-627 ger DE-627 rda eng 333.7 DE-600 43.00 bkl Schettgen, Thomas verfasserin (orcid)0000-0003-1256-1713 aut Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry 2021 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry. Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants Esser, André verfasserin aut Kraus, Thomas verfasserin aut Ziegler, Patrick verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 291 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:291 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 43.00 Umweltforschung Umweltschutz: Allgemeines AR 291
allfieldsGer	10.1016/j.chemosphere.2021.132722 doi (DE-627)ELV00728182X (ELSEVIER)S0045-6535(21)03194-5 DE-627 ger DE-627 rda eng 333.7 DE-600 43.00 bkl Schettgen, Thomas verfasserin (orcid)0000-0003-1256-1713 aut Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry 2021 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry. Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants Esser, André verfasserin aut Kraus, Thomas verfasserin aut Ziegler, Patrick verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 291 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:291 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 43.00 Umweltforschung Umweltschutz: Allgemeines AR 291
allfieldsSound	10.1016/j.chemosphere.2021.132722 doi (DE-627)ELV00728182X (ELSEVIER)S0045-6535(21)03194-5 DE-627 ger DE-627 rda eng 333.7 DE-600 43.00 bkl Schettgen, Thomas verfasserin (orcid)0000-0003-1256-1713 aut Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry 2021 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry. Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants Esser, André verfasserin aut Kraus, Thomas verfasserin aut Ziegler, Patrick verfasserin aut Enthalten in Chemosphere Amsterdam [u.a.] : Elsevier Science, 1972 291 Online-Ressource (DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961 1879-1298 nnns volume:291 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 43.00 Umweltforschung Umweltschutz: Allgemeines AR 291
language	English
source	Enthalten in Chemosphere 291 volume:291
sourceStr	Enthalten in Chemosphere 291 volume:291
format_phy_str_mv	Article
bklname	Umweltforschung Umweltschutz: Allgemeines
institution	findex.gbv.de
topic_facet	Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants
dewey-raw	333.7
isfreeaccess_bool	false
container_title	Chemosphere
authorswithroles_txt_mv	Schettgen, Thomas @@aut@@ Esser, André @@aut@@ Kraus, Thomas @@aut@@ Ziegler, Patrick @@aut@@
publishDateDaySort_date	2021-01-01T00:00:00Z
hierarchy_top_id	306354217
dewey-sort	3333.7
id	ELV00728182X
language_de	englisch
fullrecord	<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">ELV00728182X</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230524123222.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">230506s2021 xx \|\|\|\|\|o 00\| \|\|eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1016/j.chemosphere.2021.132722</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)ELV00728182X</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(ELSEVIER)S0045-6535(21)03194-5</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rda</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">333.7</subfield><subfield code="q">DE-600</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">43.00</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Schettgen, Thomas</subfield><subfield code="e">verfasserin</subfield><subfield code="0">(orcid)0000-0003-1256-1713</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2021</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">nicht spezifiziert</subfield><subfield code="b">zzz</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Biological monitoring</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">PCB</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Exposure assessment</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Mixtures</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Persistent organic pollutants</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Esser, André</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Kraus, Thomas</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Ziegler, Patrick</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Chemosphere</subfield><subfield code="d">Amsterdam [u.a.] : Elsevier Science, 1972</subfield><subfield code="g">291</subfield><subfield code="h">Online-Ressource</subfield><subfield code="w">(DE-627)306354217</subfield><subfield code="w">(DE-600)1496851-4</subfield><subfield code="w">(DE-576)081952961</subfield><subfield code="x">1879-1298</subfield><subfield code="7">nnns</subfield></datafield><datafield tag="773" ind1="1" ind2="8"><subfield code="g">volume:291</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_USEFLAG_U</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SYSFLAG_U</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ELV</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-PHA</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OPC-GGO</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_20</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_22</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_23</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_24</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_31</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_32</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_40</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_60</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_62</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_63</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_69</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_70</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_73</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_74</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_90</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_95</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_100</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_105</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_110</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_151</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_224</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_370</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_602</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_702</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2003</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2004</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2005</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2011</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2014</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2015</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2020</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2021</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2025</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2027</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2034</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2038</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2044</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2048</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2049</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2050</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2056</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2059</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2061</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2064</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2065</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2068</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2111</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2112</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2113</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2118</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2122</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2129</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2143</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2147</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2148</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2152</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2153</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2190</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2336</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2507</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2522</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4035</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4037</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4112</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4125</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4126</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4242</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4251</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4305</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4313</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4323</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4324</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4325</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4326</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4333</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4334</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4335</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4338</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4393</subfield></datafield><datafield tag="936" ind1="b" ind2="k"><subfield code="a">43.00</subfield><subfield code="j">Umweltforschung</subfield><subfield code="j">Umweltschutz: Allgemeines</subfield></datafield><datafield tag="951" ind1=" " ind2=" "><subfield code="a">AR</subfield></datafield><datafield tag="952" ind1=" " ind2=" "><subfield code="d">291</subfield></datafield></record></collection>
author	Schettgen, Thomas
spellingShingle	Schettgen, Thomas ddc 333.7 bkl 43.00 misc Biological monitoring misc PCB misc Exposure assessment misc Mixtures misc Persistent organic pollutants Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry
authorStr	Schettgen, Thomas
ppnlink_with_tag_str_mv	@@773@@(DE-627)306354217
format	electronic Article
dewey-ones	333 - Economics of land & energy
delete_txt_mv	keep
author_role	aut aut aut aut
collection	elsevier
remote_str	true
illustrated	Not Illustrated
issn	1879-1298
topic_title	333.7 DE-600 43.00 bkl Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry Biological monitoring PCB Exposure assessment Mixtures Persistent organic pollutants
topic	ddc 333.7 bkl 43.00 misc Biological monitoring misc PCB misc Exposure assessment misc Mixtures misc Persistent organic pollutants
topic_unstemmed	ddc 333.7 bkl 43.00 misc Biological monitoring misc PCB misc Exposure assessment misc Mixtures misc Persistent organic pollutants
topic_browse	ddc 333.7 bkl 43.00 misc Biological monitoring misc PCB misc Exposure assessment misc Mixtures misc Persistent organic pollutants
format_facet	Elektronische Aufsätze Aufsätze Elektronische Ressource
format_main_str_mv	Text Zeitschrift/Artikel
carriertype_str_mv	cr
hierarchy_parent_title	Chemosphere
hierarchy_parent_id	306354217
dewey-tens	330 - Economics
hierarchy_top_title	Chemosphere
isfreeaccess_txt	false
familylinks_str_mv	(DE-627)306354217 (DE-600)1496851-4 (DE-576)081952961
title	Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry
ctrlnum	(DE-627)ELV00728182X (ELSEVIER)S0045-6535(21)03194-5
title_full	Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry
author_sort	Schettgen, Thomas
journal	Chemosphere
journalStr	Chemosphere
lang_code	eng
isOA_bool	false
dewey-hundreds	300 - Social sciences
recordtype	marc
publishDateSort	2021
contenttype_str_mv	zzz
author_browse	Schettgen, Thomas Esser, André Kraus, Thomas Ziegler, Patrick
container_volume	291
class	333.7 DE-600 43.00 bkl
format_se	Elektronische Aufsätze
author-letter	Schettgen, Thomas
doi_str_mv	10.1016/j.chemosphere.2021.132722
normlink	(ORCID)0000-0003-1256-1713
normlink_prefix_str_mv	(orcid)0000-0003-1256-1713
dewey-full	333.7
author2-role	verfasserin
title_sort	plasma levels of unintentionally produced non-aroclor polychlorinated biphenyl (pcb) congeners in workers from the silicone rubber industry
title_auth	Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry
abstract	The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry.
abstractGer	The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry.
abstract_unstemmed	The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry.
collection_details	GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OLC-PHA SSG-OPC-GGO GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393
title_short	Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry
remote_bool	true
author2	Esser, André Kraus, Thomas Ziegler, Patrick
author2Str	Esser, André Kraus, Thomas Ziegler, Patrick
ppnlink	306354217
mediatype_str_mv	c
isOA_txt	false
hochschulschrift_bool	false
doi_str	10.1016/j.chemosphere.2021.132722
up_date	2024-07-07T00:13:27.084Z
_version_	1803877044280360960
fullrecord_marcxml	<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">ELV00728182X</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230524123222.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">230506s2021 xx \|\|\|\|\|o 00\| \|\|eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1016/j.chemosphere.2021.132722</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)ELV00728182X</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(ELSEVIER)S0045-6535(21)03194-5</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rda</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">333.7</subfield><subfield code="q">DE-600</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">43.00</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Schettgen, Thomas</subfield><subfield code="e">verfasserin</subfield><subfield code="0">(orcid)0000-0003-1256-1713</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2021</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">nicht spezifiziert</subfield><subfield code="b">zzz</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">The unintentional release of non-Aroclor-PCBs 47, PCB 68 and PCB 51 by a silicone manufacturing company in North Rhine-Westphalia, Germany, due to the use of bis-(2,4-dichlorobenzoyl)peroxide (2,4-DCBP) as an initiator has raised serious concerns about the possible uptake of these congeners by workers in silicone rubber production. We have conducted a pilot study in Germany to quantify these congeners in plasma samples of employees working in and handling silicone rubber during production and electrical cable manufacturing. A total of 117 plasma samples were collected from workers in 7 companies and 84 plasma samples from control subjects not working in silicone industry. PCB 47 and PCB 68 were detected in plasma above the limit of quantification (0.01 μg/L) in 84% and 66% of the silicone industry workers, respectively, whereas both congeners were undetectable in plasma of the control group. The maximum levels for PCB 47 were 2.56 μg/L and for PCB 68 were 0.42 μg/L. PCB 51 could not be determined in any plasma sample. Plasma samples of workers making electric cables had in general lower levels than those from workers making silicone rubber. Due to the high persistence of PCBs and the poorly defined toxicological properties of PCB 47 and PCB 68, a replacement of 2,4-DCBP as initiator in silicone rubber production should be considered. Given the large market for silicone products, our results might have a global impact on silicone industry.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Biological monitoring</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">PCB</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Exposure assessment</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Mixtures</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Persistent organic pollutants</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Esser, André</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Kraus, Thomas</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Ziegler, Patrick</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Chemosphere</subfield><subfield code="d">Amsterdam [u.a.] : Elsevier Science, 1972</subfield><subfield code="g">291</subfield><subfield code="h">Online-Ressource</subfield><subfield code="w">(DE-627)306354217</subfield><subfield code="w">(DE-600)1496851-4</subfield><subfield code="w">(DE-576)081952961</subfield><subfield code="x">1879-1298</subfield><subfield code="7">nnns</subfield></datafield><datafield tag="773" ind1="1" ind2="8"><subfield code="g">volume:291</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_USEFLAG_U</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SYSFLAG_U</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ELV</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-PHA</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OPC-GGO</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_20</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_22</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_23</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_24</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_31</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_32</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_40</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_60</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_62</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_63</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_69</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_70</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_73</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_74</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_90</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_95</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_100</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_105</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_110</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_151</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_224</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_370</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_602</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_702</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2003</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2004</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2005</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2011</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2014</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2015</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2020</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2021</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2025</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2027</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2034</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2038</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2044</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2048</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2049</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2050</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2056</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2059</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2061</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2064</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2065</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2068</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2111</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2112</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2113</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2118</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2122</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2129</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2143</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2147</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2148</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2152</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2153</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2190</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2336</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2507</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2522</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4035</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4037</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4112</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4125</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4126</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4242</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4251</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4305</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4313</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4323</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4324</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4325</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4326</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4333</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4334</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4335</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4338</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4393</subfield></datafield><datafield tag="936" ind1="b" ind2="k"><subfield code="a">43.00</subfield><subfield code="j">Umweltforschung</subfield><subfield code="j">Umweltschutz: Allgemeines</subfield></datafield><datafield tag="951" ind1=" " ind2=" "><subfield code="a">AR</subfield></datafield><datafield tag="952" ind1=" " ind2=" "><subfield code="d">291</subfield></datafield></record></collection>
score	7.400259

Nicht das Richtige dabei?

Schreiben Sie uns!

Plasma levels of unintentionally produced non-Aroclor polychlorinated biphenyl (PCB) congeners in workers from the silicone rubber industry

Nicht das Richtige dabei?

Zugang & Verfügbarkeit

Vorhandene Bände

Nicht das Richtige dabei?