Jürgen Wittsiepe
Ruhr University Bochum
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Environmental Health Perspectives | 2011
Eva Govarts; Mark J. Nieuwenhuijsen; Greet Schoeters; Ferran Ballester; Karolien Bloemen; Michiel R. de Boer; Cécile Chevrier; Merete Eggesbø; Mònica Guxens; Ursula Krämer; Juliette Legler; David Martinez; Lubica Palkovicova; Evridiki Patelarou; Ulrich Ranft; Arja Rautio; Maria Skaalum Petersen; Rémy Slama; Hein Stigum; Gunnar Toft; Tomas Trnovec; Stéphanie Vandentorren; Pal Weihe; Nynke Weisglas Kuperus; Michael Wilhelm; Jürgen Wittsiepe; Jens Peter Bonde
Objectives: Exposure to high concentrations of persistent organochlorines may cause fetal toxicity, but the evidence at low exposure levels is limited. Large studies with substantial exposure contrasts and appropriate exposure assessment are warranted. Within the framework of the EU (European Union) ENRIECO (ENvironmental Health RIsks in European Birth Cohorts) and EU OBELIX (OBesogenic Endocrine disrupting chemicals: LInking prenatal eXposure to the development of obesity later in life) projects, we examined the hypothesis that the combination of polychlorinated biphenyls (PCBs) and dichlorodiphenyldichloroethylene (DDE) adversely affects birth weight. Methods: We used maternal and cord blood and breast milk samples of 7,990 women enrolled in 15 study populations from 12 European birth cohorts from 1990 through 2008. Using identical variable definitions, we performed for each cohort linear regression of birth weight on estimates of cord serum concentration of PCB-153 and p,p´-DDE adjusted for gestational age and a priori selected covariates. We obtained summary estimates by meta-analysis and performed analyses of interactions. Results: The median concentration of cord serum PCB-153 was 140 ng/L (range of cohort medians 20–484 ng/L) and that of p,p´-DDE was 528 ng/L (range of cohort medians 50–1,208 ng/L). Birth weight decreased with increasing cord serum concentration of PCB-153 after adjustment for potential confounders in 12 of 15 study populations. The meta-analysis including all cohorts indicated a birth weight decline of 150 g [95% confidence interval (CI): –250, –50 g] per 1-µg/L increase in PCB-153, an exposure contrast that is close to the range of exposures across the cohorts. A 1-µg/L increase in p,p´-DDE was associated with a 7-g decrease in birth weight (95% CI: –18, 4 g). Conclusions: The findings suggest that low-level exposure to PCB (or correlated exposures) impairs fetal growth, but that exposure to p,p´-DDE does not. The study adds to mounting evidence that low-level exposure to PCBs is inversely associated with fetal growth.
Chemosphere | 2000
Jürgen Wittsiepe; Petra Schrey; Ulrich Ewers; Fidelis Selenka; Michael Wilhelm
744 whole blood samples of normal subjects from Germany collected in 1989-1998 have been analyzed for polychlorinated dibenzo-p-dioxins (PCDD) and dibenzofurans (PCDF) by capillary gas chromatography/high resolution mass spectrometry. Over the examined time period a continuous decrease of the PCDD/F concentrations in human blood was observed. The mean levels found were 43.7 pg I-TEq/g (lipid basis) in 1989 and 20.7 pg I-TEq/g (lipid basis) in 1996/98 [median: 42.2 and 19.4]. The reduction to about the half was found for most congeners. Each one-year subset of the collective and the entire collective shows a positive correlation of the PCDD/F blood levels with age for most of the congeners, the sum values and the calculated toxicity equivalents. For statistical evaluation a multiplicative model was used: Concentration = A x Age(B). The correlation is mostly pronounced for lower chlorinated PCDD and for 2,3,4,7,8-PentaCDF. The PCDD/F concentrations in human blood in relation to the year of examination and the age of the subjects can be described by a linear model: I-TEq [pg/g (lipid basis)] = 6176 - 3.097 x Year + 0.6482 x Age or by a multiplicative model: I-TEq [pg/g(lipid basis)] = 10(89.08-0.04415 x Year + 0.008468 x Age).
International Journal of Hygiene and Environmental Health | 2012
Monika Kasper-Sonnenberg; Holger M. Koch; Jürgen Wittsiepe; Michael Wilhelm
Phthalates are used ubiquitously and human exposure is widespread. Some phthalates are anti-androgens and have to be regarded as reproductive and developmental toxicants. In the Duisburg birth cohort study we examine the associations between hormonally active environmental agents and child development. Here we report the concentrations of 21 primary and secondary phthalate metabolites from seven low molecular weight (LMW) phthalates (DMP, DEP, BBzP, DiBP, DnBP, DCHP, DnPeP) and five high-molecular weight (HMW) phthalates (DEHP, DiNP, DiDP, DPHP, DnOP) in 208 urine samples from 104 mothers and their school-aged children. Analysis was performed by multidimensional liquid chromatography coupled to tandem mass spectrometry (LC/LC-MS/MS), using internal isotope-labeled standards. In both children and mothers, 18 out of 21 phthalate metabolites were detected above the limits of quantification (between 0.2 and 1.0 μg/l) in nearly all urine samples. Among the LMW phthalates, the excretion level (geometric mean) of the ΣDiBP metabolites was most prominent in children (103.9 μg/l), followed by ΣDnBP (56.5 μg/l), and MEP (39.1 μg/l). In mothers ΣDiBP (66.6 μg/l) was highest, followed by MEP (50.5 μg/l), and ΣDnBP (36.0 μg/l). Among the HMW phthalates, ΣDEHP was highest in children and mothers (55.7/28.9 μg/l). Compared to reference values derived from the German Human Biomonitoring Commission, childrens metabolite concentrations were within background levels, whereas for mothers considerably higher exposure to the LMW phthalates DnBP and DiBP, and the HMW phthalate DEHP was detected (MiBP: 10.7%; MnBP: 11.7%; ΣDEHP: 23.3% of the samples were above the reference values). The LMW metabolites from DMP, DiBP, and DnBP, and the HMW metabolites from DEHP and DiNP were correlated between the mothers and children, probably indicating shared exposure in the immediate surrounding environment. Children showed higher excretion levels for most of the secondary metabolites than mothers, confirming previous findings on higher oxidized metabolite levels in children. The LMW metabolites ΣDiBP, ΣDnBP, and MMP, and the HMW metabolites ΣDEHP were negatively associated with childrens age. The LMW metabolites ΣDiBP, ΣDnBP, and MBzP were inversely associated with body mass index of the children. The LMW ΣDiBP metabolites revealed a significant association with nicotine metabolites in urine from both children and mothers. Further analyses are ongoing to study long-term phthalate exposure and the associations with puberty outcome in these children.
Toxicology Letters | 2009
Nicola Höfer; Patrick Diel; Jürgen Wittsiepe; Michael Wilhelm; Gisela H. Degen
The toxic heavy metal cadmium (Cd) is regarded as a potential endocrine disruptor, since Cd exerts estrogen-like activity in vitro and can elicit some typical estrogenic responses in rodents upon intraperitoneal (i.p.) injection. But estrogenic effects have not been documented in vivo with other more relevant routes of exposure, although it is known that Cd absorption and distribution in the body is strongly affected by the application route. Therefore, we investigated its hormonal activity in ovariectomized Wistar rats after oral administration of CdCl(2) (0.05-4 mg/kg b.w. on 3 days by gavage and 0.4-9 mg/kg b.w. for 4 weeks in drinking water) in comparison with i.p. injection of CdCl(2) (0.00005-2 mg/kg b.w.). Uterus wet weight, height of uterine epithelium, and modulation of estrogen-regulated gene expression, i.e. uterine complement component 3 (C3), were determined, and also Cd-levels in uterus and liver were measured by atomic absorption spectrometry. The analysis revealed pronounced differences in Cd tissue levels and hormonal potency for the two routes of administration: a single i.p. injection of Cd increased dose-dependently uterine wet weight and thickness of the uterine epithelium. Interestingly, C3 mRNA expression in the uterus was down regulated at low doses of CdCl(2) (0.00005-0.05 mg/kg b.w.), but strongly stimulated at the highest dose of 2 mg/kg b.w. Other than i.p. injection, oral treatment with Cd, by gavage or in drinking water, did neither increase uterine wet weights nor epithelial thickness. But, both 3-day- and 4-week oral Cd administration resulted in a dose-dependent stimulation of C3 expression in the uterus, significant at and above 0.5 mg/kg b.w. In summary, our data demonstrate an estrogenic effect in the uterus upon i.p. injection of Cd, but considerably lower hormonal potency with oral administration: short and long-term oral treatment with Cd did not affect uterus weight or histology, whilst on the molecular level, an induction of estrogen sensitive uterine gene expression was observed, albeit at dose levels far exceeding those of dietary exposure in humans.
International Journal of Hygiene and Environmental Health | 2004
Annett Hilbig; Natja Freidank; Mathilde Kersting; Michael Wilhelm; Jürgen Wittsiepe
Dietary intakes of acrylamide for the general population were estimated by FAO/WHO to be in the range of 0.3 to 0.8 microg/(kg(bw) *d). It was supposed that children and adolescents would generally have intakes twice to three times higher than adults. However, relevant data is rare. Therefore, 3- or 7-day dietary records (n = 2956) from infants, children and adolescents aged 0.5 to 18 years from the DONALD study (2001) and other studies (RUB studies) were evaluated to estimate the potential dietary intake of acrylamide. Statistical data of the intake of 6 food groups relevant for acrylamide exposure were combined with available data for ranges of acrylamide concentrations in more than 1500 foods in Germany. Scenarios were calculated assuming minimum, median and maximum acrylamide concentration in food groups. Assuming median (minimum; maximum) acrylamide concentrations in foods and mean consumed food amounts, the calculated intake of acrylamide ranged from 0.21-0.43 (0.12-0.19; 0.98-1.79) microg/(kg(bw) *d) between the age groups from <1 to <19 years in the DONALD study and was 0.61 (0.21; 2.58) microg/(kg(bw) *d) from 1 to <7 years in the RUB studies. The highest intake was calculated for children aged 1-<7 years. The highest proportions of total intake of acrylamide came from the intake of commercial baby food (86-91%) in infants, and bread (18-46%), pastries (16-35%), and potato products (7-35%) in children and adolescents, depending on scenario and age. Our estimated data are in the range of reports from the literature for adolescents and adults in Germany and other European countries and lower than reports for infants. Our results do not confirm that children and adolescents will have higher exposures to acrylamide than adults. Practical suggestions to lower the risk of acrylamide exposure by food without decreasing the quality of the nutrition in the diet are given.
Science of The Total Environment | 2002
Michael Wilhelm; Jürgen Wittsiepe; Petra Schrey; Ursula Budde
The dietary intake of cadmium was studied among children and adults from Germany. The study area comprised the highly industrialized Ruhr district as well as the North Sea island Amrum. A total of 229 duplicate samples were collected from 49 individuals between December 1994 and May 1995. The sampling period for each participant was either 3 or 7 days. Cadmium concentrations in duplicate samples were measured by atomic absorption spectrometry. The daily cadmium intakes (geometric mean) for 4 different groups of individuals distributed as follows: for small children (mean age: 1.8 years) from the Ruhr district 0.17 microg/(kg(bw) x day) [range: 0.02-1.62 microg/(kg(bw) x day)], for children (mean age: 3.8 years) from the Ruhr district 0.49 microg/(kg(bw) x day) [range: 0.11-2.06 microg/(kg(bw) x day)], for children (mean age: 3.9 years) living on the North Sea island Amrum 0.35 microg/(kg(bw)-day) [range: 0.09-1.13 microg/ (kg(bw) x day)] and for adults (mean age: 40.9 years) from the Ruhr district 0.37 microg/(kg(bw) x day) [range: 0.05-1.32 microg/(kg(bw) x day)]. Compared to the provisional tolerable weekly intake (PTWI) of 7 microg/(kg(bw) x week) proposed by the WHO the dietary intake of cadmium was rather high. The geometric mean and maximum intake values for the different groups ranged between 24.3-55.7% and 62.7-120.7 respectively of the PTWI. We therefore conclude, that the cadmium exposure of the population needs to be reduced in order to minimize the risk of adverse health effects related to this metal.
International Journal of Hygiene and Environmental Health | 2013
Kerstin Becker; C. Schroeter-Kermani; Margarete Seiwert; Maria Rüther; André Conrad; Christine Schulz; Michael Wilhelm; Jürgen Wittsiepe; A. Günsel; L. Dobler; Marike Kolossa-Gehring
The German system of a health-related environmental monitoring is based upon two instruments: The German Environmental Survey (GerES) and the Environmental Specimen Bank (ESB). The ESB is a tool to describe time trends of human exposure. Each year approx. 500 students from 4 sampling locations are analysed for their heavy metal contents in blood, blood plasma, and urine. GerES is a nationwide representative cross-sectional study that has been conducted four times up to now. Both instruments have been used to measure heavy metals over the last decades and thus provide complementary information. Both instruments are useful to describe time trends. However, combining the two has an added value, which is demonstrated for heavy metals for the first time in this paper. Major results and the changing importance of sources of exposure to heavy metals (Pb, Cd, Hg, Au, Pt, U and Ni) are shown. This leads to the following conclusion about the todays relevance of exposure in Germany. For the study participants of the city of Muenster, lead in whole blood decreased from about 70 μg/l in 1981 to levels below 15 μg/l in 2009. GerES data of young adults confirmed this time trend and GerES IV on children revealed the decreasing relevance of lead in outdoor air and in drinking water. The concentrations of mercury in urine decreased because in Germany it is no longer recommended to use amalgam fillings for children. However, GerES IV and ESB data also demonstrate that despite the decline of these heavy metals exposures to nickel and uranium originating from drinking water are still of importance.
International Journal of Hygiene and Environmental Health | 2000
Petra Schrey; Jürgen Wittsiepe; Ursula Budde; Birger Heinzow; Michael Wilhelm
The dietary intake of metals was studied in seven male and seven female children at the age of 1.5 to 5.3 years living in a remote area of Germany, the North Sea island Amrum. The dietary intake of lead and cadmium was measured by a seven-day-duplicate study using atomic absorption spectrometry. The dietary intake of copper and zinc were calculated from food diaries. The median lead and cadmium intakes were 2.1 micrograms/(kgbw x week) [range: 0.63-5.1 micrograms/(kgbw x week)] and 2.7 micrograms/(kgbw x week) [range: 1.7-4.4 micrograms/(kgbw x week)]. The median daily intake of copper and zinc were 1.1 mg/d (range: 0.54-2.5 mg/d) and 5.7 mg/d (range: 2.7-14 mg/d). Compared to the provisional tolerable weekly intake (PTWI) of 25 micrograms/(kgbw x week) proposed by the WHO the dietary intake of lead was low. The median amounted to 8.5% and the maximum to 20% of the PTWI. The cadmium intake was comparatively high. The median amounted to 39% and the maximum to 63% of the PTWI [7 micrograms/(kgbw x week)]. The median intake of copper was in the range of the values recommended by the German Society of Nutrition (0.7-1.0 mg/d and 1.0-1.5 mg/d for children at the age of 1-< 4 years and 4-< 7 years). Twenty-three percent of the calculated intakes were below these values. The median intake of zinc however did not reach the recommended dietary intake of 7 and 10 mg/d for children at the age of 1-< 4 years and 4-< 7 years.
International Journal of Hygiene and Environmental Health | 2014
Rebecca K. Moos; Jürgen Angerer; Jürgen Wittsiepe; Michael Wilhelm; Thomas Brüning; Holger M. Koch
We developed a fast, selective and sensitive on-line LC/LC-MS/MS method for the simultaneous determination of nine parabens and seven environmental phenols in urine. Parabens are widely used as antimicrobial preservatives. Bisphenol A, triclosan, triclocarban, 2-phenylphenol, and benzophenones are used inter alia in disinfectants, sunscreens and in polymers. Some of these substances are suspected endocrine disruptors. Limits of quantification and analytical quality criteria fully met the needs for determining exposure levels occurring in the general population. We analyzed 157 spot urine samples from the general German population (59 females, 39 males and 59 children). For the parabens, we found methyl, ethyl and n-propyl paraben with high detection rates (77-98%), followed by n-butyl (36%), iso-butyl (17%), iso-propyl (3%) and benzyl paraben (3%). We detected no pentyl and heptyl paraben. Urinary concentrations were highest for methyl paraben (median 24.5 μg/L; 95th percentile 379 μg/L) followed by ethyl (1.4 μg/L; 35.2 μg/L) and n-propyl paraben (1.2 μg/L; 68.1 μg/L). Other environmental phenols with high detection rates were BPA (95%), triclosan (45%) and benzophenone 1 and 3 (26%). For most of the parabens/environmental phenols we found higher urinary levels in females than in males or children, probably due to differences in (personal care) product use. However, high levels (in the mg/L range) were also observed in children. Exposure to the above substances is occurring worldwide. Differences between countries do seem to exist and might be caused by different product compositions or different use habits. Human metabolism data is urgently needed to extrapolate from urinary biomarker levels to doses actually taken up.
Environmental Health Perspectives | 2015
Nina Iszatt; Hein Stigum; Marc-André Verner; Richard A. White; Eva Govarts; Lubica Palkovicova Murinova; Greet Schoeters; Tomas Trnovec; Juliette Legler; Fabienne Pelé; Jérémie Botton; Cécile Chevrier; Jürgen Wittsiepe; Ulrich Ranft; Stéphanie Vandentorren; Monika Kasper-Sonnenberg; Claudia Klümper; Nynke Weisglas-Kuperus; Anuschka Polder; Merete Eggesbø
Background Infant exposure to persistent organic pollutants (POPs) may contribute to obesity. However, many studies so far have been small, focused on transplacental exposure, used an inappropriate measure to assess postnatal exposure through breastfeeding if any, or did not discern between prenatal and postnatal effects. Objectives We investigated prenatal and postnatal exposure to POPs and infant growth (a predictor of obesity). Methods We pooled data from seven European birth cohorts with biomarker concentrations of polychlorinated biphenyl 153 (PCB-153) (n = 2,487), and p,p´-dichlorodiphenyldichloroethylene (p,p´-DDE) (n = 1,864), estimating prenatal and postnatal POPs exposure using a validated pharmacokinetic model. Growth was change in weight-for-age z-score between birth and 24 months. Per compound, multilevel models were fitted with either POPs total exposure from conception to 24 months or prenatal or postnatal exposure. Results We found a significant increase in growth associated with p,p´-DDE, seemingly due to prenatal exposure (per interquartile increase in exposure, adjusted β = 0.12; 95% CI: 0.03, 0.22). Due to heterogeneity across cohorts, this estimate cannot be considered precise, but does indicate that an association with infant growth is present on average. In contrast, a significant decrease in growth was associated with postnatal PCB-153 exposure (β = –0.10; 95% CI: –0.19, –0.01). Conclusion To our knowledge, this is the largest study to date of POPs exposure and infant growth, and it contains state-of-the-art exposure modeling. Prenatal p,p´-DDE was associated with increased infant growth, and postnatal PCB-153 with decreased growth at European exposure levels. Citation Iszatt N, Stigum H, Verner MA, White RA, Govarts E, Palkovicova Murinova L, Schoeters G, Trnovec T, Legler J, Pelé F, Botton J, Chevrier C, Wittsiepe J, Ranft U, Vandentorren S, Kasper-Sonnenberg M, Klümper C, Weisglas-Kuperus N, Polder A, Eggesbø M, OBELIX. 2015. Prenatal and postnatal exposure to persistent organic pollutants and infant growth: a pooled analysis of seven European birth cohorts. Environ Health Perspect 123:730–736; http://dx.doi.org/10.1289/ehp.1308005