| 1. |
- Hagmar, Lars, et al.
(författare)
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Tidstrender för halter av persistenta klororganiska miljögifter i blod hos vuxna svenska män i relation till konsumtion av fet östersjöfisk
- 2004
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Rapport (övrigt vetenskapligt/konstnärligt)abstract
- Det har skett en signifikant genomsnittlig minskning med 34 till 55 % av serumhalterna av CB-153, p,p´-DDE och HCB under perioden 1991 till 2001 bland 39 medelålders svenska män, varav en del med hög konsumtion av fet östersjöfisk. Detta kunde inte förklaras med förändrad fiskkonsumtion över tiden. Däremot förklarade en ökad kroppsvikt en del av minskningen, genom en ”utspädningseffekt” (större distributionsvolym). Det är sannolikt att en minskad förorening av animaliska livsmedel med dessa POPs under senare år bidragit till de sjunkande halterna i serum. I motsats till resultaten för CB-153, p,p´-DDE och HCB förelåg det inte någon signifikant tidstrend för TEQ för PCDD eller PCDF I serum bland 26 medelålders svenska män, trots en längre uppföljningsperiod (1987 till 2002). För enskilda PCDD/F kongeners noterades såväl minskningar som ökningar över tiden. Resultaten ger vid handen att dioxinbelastningen varit oförändrad under den senaste 15 års perioden.
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| 2. |
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| 3. |
- Remberger, Mikael, et al.
(författare)
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Screening of Emerging Brominated Flame Retardants (BFRs) and Polybrominated dibenzofurans (PBDFs)
- 2014
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Rapport (övrigt vetenskapligt/konstnärligt)abstract
- As an assignment from the Swedish Environmental Protection Agency, a screening study of selected emerging brominated flame retardants (BFRs) and polybrominated dibenzofurans (PBDFs) has been carried out. Additional substances in the screening were polybrominated diphenyl ethers (PBDEs), polybrominated dibenzodioxins (PBDDs) and chlorinated dioxins and furans (PCDDs and PCDFs).The overall objective of this screening study was to determine the concentrations of selected BFRs and PBDFs in a variety of media in the Swedish environment. Additional aims were to assess possible emission sources and to highlight important transport pathways in the environment including large scale transport. An issue for the screening was also to investigate the presences of the BFRs in biota to give an indication if they pose an environmental risk. Possible human exposure was investigated by analysing BFRs in human blood samples and PBDFs in human milk samples.Measurements have been carried out both at background- and urban sites. The sampling was mainly performed at the Swedish west coast with Göteborg representing the urban area. Sediment and biota was sampled in the estuary of Göta Älv and in a background area.For identification of pathways to the environment storm water/sludge and samples from WWTPs were collected. Dust samples from different indoor environments were taken both at public spaces and in homes. Air and dust samples were collected at a recycling industry for electronic waste. Fire extinguishing water from a fire at a recycling industry was included in the sampling program.The emerging BFRs, PBDEs and PBDFs occurred in "high" concentrations in air and dust from the recycling industry. The occurrence of BFRs at this electronic waste facility shows that electronic articles contain these chemicals. BDE-209 and DBDPE were found in highest concentrations. DBDPE has similar applications as BDE-209 and it has been marketed as a general substitute for this chemical. The occurrence of PBDFs may indicate that the BFRs are contaminated or that PBDEs are transformed to PBDFs in the recycling processes.The presence of both the emerging BFRs and PBDEs in dust collected in a "new private car" shows that theses flame retardants are used in textiles and plastic details in newly manufactured cars. DBDPE and BDE-209 which are used as flame retardants in textiles occurred in high concentration. The simultaneous occurrence of high levels of PBDFs indicates presence in BFR formulations.The occurrences of the included BFRs in dust from different indoor environments indicates a wide application of these chemicals in articles and household products and that diffuse emissions of BFRs from consumer products may take place in the indoor environment. The differences in the distribution among the BFRs for the different dust samples indicate that tHigher ratios of PBDFs vs. BDE-209 were found in dust from environments that are likely to contain BFR containing plastics (offices and recycling facilities) than in dust from environments containing BFR treated textile products (car and conference center interiors). This may indicate that PBDFs are formed during production or use of flame retarded plastics.The emissions of BFRs and PBDFs will take place both to air and water. BFRs and PBDFs emitted indoors to air and to settled dust may via ventilation be transported to outdoor air. The presence of these pollutants in influent, effluent and sludge from municipal WWTPs also indicate that diffusive emissions from household products occur and that these chemicals may be emitted to the environment from WWTPs. The occurrence of the BFRs and PBDD/Fs in storm water and fire extinguishing water shows that this may also be pathways to the environment.Thus, the emerging BFRs and PBDFs were generally found in samples from WWTPs, storm water, indoor air and dust, indicating that they may be emitted and transported to the environment via these sources and pathways.Several of the emerging BFRs occurred in all the included environmental matrices except in atmospheric deposition. The concentrations in samples at urban sites were higher compared to background samples.Most of the emerging BFRs were detected in urban air, in the same levels or somewhat lower than BDE-47, -100 and -99. BDE-209 occurred in the highest concentrations. One of the emerging BFRs, HBB, was detected in background air, in the same concentration range as the PBDEs. It was found both at the Swedish West coast and in the remote area in Northern Finland, which shows the potential for atmospheric long range transport for HBB.PBDD/Fs were found in all air and deposition samples. There appears to be an annual variation in both PBDD/F and PCDD/F concentrations, with higher levels during winter. Significantly elevated levels were detected in May-June 2011, which coincided with extensive forest fires in southern Russia and Ukraine.In sediments, the emerging BFRs were only detected in a sample from Göta Älv near a former industrial site where they occurred in the same concentration level as the penta-BDEs.The occurrence of emerging BFRs in biota from background sites shows that these chemicals like the PBDEs are further spread to the ecosystem. The distribution of the BFRs differed between the various species as well as among the different sampling sites.The only emerging BFR detected in human sera was PBEB, which occurred in one out of 15 samples. PCDD/Fs were found in all human milk samples, but no PBDD/Fs were detected.
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| 4. |
- Rylander, Lars, et al.
(författare)
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Intra-individual variations and temporal trends in dioxin levels in human blood 1987-2002
- 2009
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Ingår i: Chemosphere. - Oxford : Pergamon Press. - 0045-6535 .- 1879-1298. ; 76:11, s. 1557-1562
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Tidskriftsartikel (refereegranskat)abstract
- Objectives: In Sweden, an important source for exposure to persistent organochlorine pollutants, such as PCDD and PCDF, is through intake of fatty fish from the Baltic Sea off the Eastern coast of Sweden. The present study assesses temporal trends for human levels of PCDD/F between 1987 and 2002 among 26 men from Sweden. In addition, we investigate the impact of potential determinants (age, relative change in BMI and fish consumption) on the relatively change in individual PCDD/F congener levels between 1987 and 2002. Methods: In 1987, nine of the men did not eat fatty fish from the Baltic Sea, eight had a moderate intake, and nine were high consumers. For the same individuals,blood samples were collected in 1987 as well as in 2002, and the concentrations of seven PCDD and 10 PCDF congeners were analyzed at the same laboratory. Results: The WHO-TEQ levels for PCDD/F did not significantly change over the 15-year period. There were, however, some specific congeners that significantly had changed over time. None of the investigated determinants were associated with the change over time for the specific PCDD/F congeners. Conclusion: The present study may be of importance for risk assessment and setting standards for food contamination with PCDD/F, especially regarding intake of fatty fish from the Baltic Sea.
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| 5. |
- Rylander, Lars, et al.
(författare)
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Intra-Individual Variations and Temporal Trends in Dioxin Levels in Human Blood 1987 to 2002
- 2008
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Ingår i: Organohalogen Compounds. ; 70, s. 001240-2
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Tidskriftsartikel (refereegranskat)abstract
- In Sweden, an important source for exposure to persistent organohalogen pollutants (POP), such as PCDD and PCDF, is through intake of fatty fish from the Baltic Sea, off the Eastern coast of Sweden.1-3 The present study aimed to assess temporal trends for human levels of PCDD/F between 1987 and 2002 among 26 men from Sweden whom in 1987 had various intakes of fish from the Baltic Sea. In addition, we investigated the impact ofpotential determinants on the relatively change in individual PCDD/F congener levels between 1987 and 2002.
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