Person: Apel, Petra
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Veröffentlichung The exposure of German children and young adults to chemicals of concern(2013) Apel, Petra; Conrad, André; Fiddicke, Ulrike; Schröter-Kermani, Christa; Schulz, Christine; Seiwert, MargareteVeröffentlichung Häufig gestellte Fragen und Antworten zu Hexabromcyclododecan (HBCD)(2016) Apel, Petra; Beer, Inga; Bolland, Til; Debiak, Malgorzata; Dettling, Folke; Koch-Jugl, Juliane; Rauert, Caren; Stolzenberg, Hans-Christian; Wuttke, Joachim; Tietjen, Lars; Walther, Mareike; Wurbs, Johanna; Deutschland. UmweltbundesamtFür das Flammschutzmittel Hexabromcyclododecan (HBCD) gilt seit Frühjahr 2016 in der EU ein weitgehendes Handels- und Verwendungsverbot. HBCD war lange das wirtschaftlich wichtigste Flammschutzmittel für Polystyrol-Dämmstoffe Ń entsprechend gibt es für Dämmstoffe aus expandiertem Polystyrol (EPS) noch Übergangsregeln. Das weltweite Aus war 2013 eingeleitet worden, als HBCD unter der internationalen Stockholm-Konvention als in der Umwelt schwer abbaubarer organischer Schadstoff (POP) identifiziert wurde. Das Verbot wird zurzeit von allen an der Konvention beteiligten Staaten stufenweise eingeführt. In unserem aktualisierten Hintergrundpapier haben wir für Sie zusammengestellt, warum der Stoff nicht mehr verwendet werden soll, welche Verbote in der Europäischen Union (EU) bereits ab März 2016 gelten und wo es noch Übergangsfristen gibt. Wir erläutern, welche Alternativen vorliegen und wie HBCD-haltige Dämmstoffe zu entsorgen sind. Quelle: UmweltbundesamtVeröffentlichung Phthalate metabolites in 24-h urine samples of the German Environmental Specimen Bank (ESB) from 1988 to 2015 and a comparison with US NHANES data from 1999 to 2012(2017) Koch, Holger M.; Apel, Petra; Schütze, Andre; Conrad, André; Pälmke, Claudia; Kolossa-Gehring, Marike; Brüning, Thomas; Rüther, MariaThe German Environmental Specimen Bank (ESB) continuously collects 24-h urine samples since theearly 1980s in Germany. In this study we analyzed 300 urine samples from the years 2007 to 2015 for 21phthalate metabolites (representing exposure to 11 parent phthalates) and combined the data with twoprevious retrospective measurement campaigns (1988 to 2003 and 2002 to 2008). The combined datasetcomprised 1162 24-h urine samples spanning the years 1988 to 2015. With this detailed set of humanbiomonitoring data we describe the time course of phthalate exposure in Germany over a time frame of27 years. For the metabolites of the endocrine disrupting phthalates di(2-ethylhexyl) phthalate (DEHP),di-n-butyl phthalate (DnBP) and butylbenzyl phthalate (BBzP) we observed a roughly ten-fold decline inmedian metabolite levels from their peak levels in the late 1980s/early 1990s compared to most recentlevels from 2015. Probably, bans (first enacted in 1999) and classifications/labelings (enacted in 2001 and2004) in the European Union lead to this drop. A decline in di-isobutyl phthalate (DiBP) metabolite levelsset in only quite recently, possibly due to its later classification as a reproductive toxicant in the EU in 2009.In a considerable number of samples collected before 2002 health based guidance values (BE, HBM I) havebeen exceeded for DnBP (27.2%) and DEHP (2.3%) but also in recent samples some individual exceedancescan still be observed (DEHP 1.0%). A decrease in concentration for all low molecular weight phthalates,labelled or not, was seen in the most recent years of sampling. For the high molecular weight phthalates,DEHP seems to have been substituted in part by di-isononyl phthalate (DiNP), but DiNP metabolite levelshave also been declining in the last years. Probably, non-phthalate alternatives increasingly take overfor the phthalates in Germany. A comparison with NHANES (National Health and Nutrition ExaminationSurvey) data from the United States covering the years 1999 to 2012 revealed both similarities anddifferences in phthalate exposure between Germany and the US. Exposure to critical phthalates hasdecreased in both countries with metabolite levels more and more aligning with each other, but highmolecular weight phthalates substituting DEHP (such as DiNP) seem to become more important in theUS than in Germany.
© 2016 Elsevier GmbH. All rights reservedVeröffentlichung New HBM values for emerging substances, inventory of reference and and HBM values in force, and working principles of the German Human Biomonitoring Commission(2016) Angerer, Jürgen; Apel, Petra; Wilhelm, Michael; Kolossa-Gehring, MarikeVeröffentlichung Häufig gestellte Fragen und Antworten zu Hexabromcyclododecan (HBCD)(2015) Apel, Petra; Beer, Inga; Bolland, Til; Debiak, Malgorzata; Dettling, Folke; Koch-Jugl, Juliane; Rauert, Caren; Stolzenberg, Hans-Christian; Wuttke, Joachim; Tietjen, Lars; Walther, Mareike; Wurbs, JohannaFür das Flammschutzmittel Hexabromcyclododecan (HBCD) gilt seit Frühjahr 2016 in der EU ein weitgehendes Handels- und Verwendungsverbot. HBCD war lange das wirtschaftlich wichtigste Flammschutzmittel für Polystyrol-Dämmstoffe – entsprechend gibt es für Dämmstoffe aus expandiertem Polystyrol (EPS) noch Übergangsregeln. Das weltweite Aus war 2013 eingeleitet worden, als HBCD unter der internationalen Stockholm-Konvention als in der Umwelt schwer abbaubarer organischer Schadstoff (POP) identifiziert wurde. Das Verbot wird zurzeit von allen an der Konvention beteiligten Staaten stufenweise eingeführt. In unserem aktualisierten Hintergrundpapier haben wir für Sie zusammengestellt, warum der Stoff nicht mehr verwendet werden soll, welche Verbote in der Europäischen Union (EU) bereits ab März 2016 gelten und wo es noch Übergangsfristen gibt. Wir erläutern, welche Alternativen vorliegen und wie HBCD-haltige Dämmstoffe zu entsorgen sind.Veröffentlichung Development of a multi-compartment pharmacokinetic model to characterize the exposure to Hexamoll® DINCH®(2015) Schütze, Andre; Apel, Petra; Lorber, Matthew; Gawrych, Katarzyna; Kolossa-Gehring, Marike; Brüning, Thomas; Koch, Holger MartinWe developed and calibrated a multi compartment pharmacokinetic (PK) model to predict urinary concentrations after oral exposure of four specific DINCH metabolites: MINCH, OH-MINCH, cx-MINCH, and oxo-MINCH. This descriptive model has 4 compartments: a "stomachŁ (SC) compartment, a "holdingŁ (HC) compartment, a "bloodŁ (BC) compartment and a "bladderŁ (BLC) compartment. DINCH is assumed to first deposit into the SC, with transfer split between the HC and the BC. Unmetabolized DINCH from the HC then transfers to the BC. The DINCH metabolism is assumed to occur in the BC before excretion via the BLC. At each urination event, all the metabolite mass in the BLC is excreted. The model was calibrated using published urine metabolite data from 3 different male volunteers, each orally dosed with 50 mg DINCH. Full urine voids were taken for 48 h after dosage. The predicted values showed a good agreement with the observed urinary DINCH metabolite concentrations, with a Spearman correlation coefficient exceeding 0.7 for all oxidized metabolites. We showed the importance of a holding reservoir. Without it, a good agreement could not be found. We applied the model to a set of 24-h general population samples measured for DINCH metabolites. The model was unable to duplicate the ratio of metabolites seen in the 24-h samples. Two possibilities were offered to explain the difference: the exposure pattern in the general population did not match the oral exposure in the dosing experiments, or the long-term toxicokinetics of DINCH was not captured in the 48-h controlled dosing experiments.Quelle: http://www.sciencedirect.comVeröffentlichung Einsatz von Nanomaterialien und nanoskaligen Produkten zur Abwasserbehandlung(2015) Apel, Petra; Dubbert, Wolfgang; Schwirn, Kathrin; Klitzke, Sondra; Völker, Doris; Liesegang, Christian; Winde, ChristineDie Behandlung von belastetem Wasser vor dem Einleiten in Oberflächengewässer ist eine der global vordringlichsten Herausforderungen der Zukunft. Bestehende Verfahren zur Wasser- und Abwasseraufbereitung können durch geeignete nanotechnische Anwendungen optimiert werden, die zu einer gezielteren Entfernung von Kontaminationen, besseren Energieeffizienz und geringeren Kosten führen können. Experten prognostizieren, dass der Wassersektor neben dem Energiesektor mittel- bis langfristig mit am stärksten von innovativen Anwendungen der Nanotechnik profitieren könnte. Neben dem Nutzen der Verwendung von Nanomaterialien zur Wasserbehandlung ist auch zu berücksichtigen, dass Nanomaterialien unbeabsichtigte Wirkungen auf die Umwelt und die menschliche Gesundheit hervorrufen können. Bei der Verwendung der Nanomaterialien muss beachtet werden, dass die neuartigen Eigenschaften der Nanomaterialien gegebenenfalls auch schädliche Wirkungen auf die Umwelt und den Menschen haben können.Veröffentlichung Neue Human-Biomonitoring Methoden für möglicherweise gesundheitsrelevante Stoffe(2013) Apel, Petra; Fiddicke, UlrikeVeröffentlichung Time trend of exposure to the phthalate plasticizer substitute DINCH in Germany from 1999 to 2017: Biomonitoring data on young adults from the Environmental Specimen Bank (ESB)(2019) Kasper-Sonnenberg, Monika; Apel, Petra; Koch, Holger M.; Kolossa-Gehring, Marike; Rüther, MariaDINCH (cyclohexane-1,2-dicarboxylic acid-diisononyl ester) is a phthalate plasticizer substitute introduced into the market in 2002. It is increasingly used especially in the production of toys, food contact materials and medical devices. In this measurement campaign on 24-h urine samples of young adults (20-29 years) from the German Environmental Specimen Bank (ESB) collected in 2010, 2011, 2013, 2015 and 2017 (in total 300 samples, 60 samples/year) we analyzed three specific, oxidized DINCH metabolites (OH-MINCH: cyclohexane-1,2-dicarboxylic acid-mono(hydroxy-isononyl) ester; cx-MINCH: cyclohexane-1,2-dicarboxylic acid-mono(carboxy-isooctyl) ester, oxo-MINCH: cyclohexane-1,2-dicarboxylic acid-mono(oxo-isononyl) ester). We merged these data with earlier data of the ESB from the years 1999-2012 and are now able to report levels and time trends of internal DINCH exposure from 1999 to 2017. After first detections of the major oxidized DINCH metabolite OH-MINCH in 2006 (6.7%) detection rates rapidly increased to 43.3% in 2009, 80% in 2010 and 98.3% in 2011 and 2012. From the year 2013 on we could detect OH-MINCH in every urine sample analyzed. The median concentrations of OH-MINCH rapidly increased from 0.15 (Mü)g/L in 2010 to twice the concentration in 2011 (0.31 (Mü)g/L) with further increases in 2013 (0.37 (Mü)g/L), 2015 (0.59 (Mü)g/L) and 2017 (0.70 (Mü)g/L). Similar increases, albeit at lower detection rates and concentration levels, could be observed for cx-MINCH and oxo-MINCH. All metabolites strongly correlate with each other. For the ESB study population, DINCH exposures are still far below health based guidance values such as the German Human Biomonitoring Value (HBM-I; 4,500 (Mü)g/L for the sum of OH-MINCH and cx-MINCH) or the tolerable daily intake (TDI) of EFSA (1mg/kg/bw/d). The median daily DINCH intake (DI) calculated for 2017 was 0.23 (Mü)g/kg bw/d, thus 4,310-times lower than the TDI. The maximum DI calculated for one individual in 2012 (42.60 (Mü)g/kg bw/d) was a factor of more than 20 below the TDI. The ongoing increase in DINCH exposure needs to be closely monitored in the future, including populations with potentially higher exposures such as children. This close monitoring will enable timely exposure and risk reduction measures if exposures reached critical levels, or if new toxicological data lead to lower health based guidance values. DINCH belongs to the European Human Biomonitoring Initiative (HBM4EU) priority substances for which policy relevant questions still have to be answered. © 2019 Elsevier GmbH. All rights reserved.Veröffentlichung Answers to frequently asked questions to Hexabromocyclododecane (HBCD)(2016) Apel, Petra; Beer, Inga; Bolland, Til; Debiak, Malgorzata; Dettling, Folke; Koch-Jugl, Juliane; Rauert, Caren; Stolzenberg, Hans-Christian; Wuttke, Joachim; Tietjen, Lars; Walther, Mareike; Wurbs, Johanna; Deutschland. UmweltbundesamtIn May 2013 the chemical hexabromocyclododecane, or HBCD, was identified as a persistent organic pollutant (POP) under the international Stockholm Convention. This means that a worldwide ban on the sale and application of the chemical will soon become effective. For a long time HBCD was the most economically significant flame retardant used in polystyrene foam for insulation materials. We have compiled information about why the chemical will no longer be used, what transitional phases are likely to be in effect in the EU, what the alternatives are, and how to dispose of insulation materials which contain HBCD. Quelle: Umweltbundesamt