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 1.0μg/l) in nearly all urine samples. Among the LMW phthalates, the excretion level (geometric mean) of the ΣDiBP metabolites was most prominent in children (103.9μg/l), followed by ΣDnBP (56.5μg/l), and MEP (39.1 μg/l). In mothers ΣDiBP (66.6μg/l) was highest, followed by MEP (50.5μg/l), and ΣDnBP (36.0μg/l). Among the HMW phthalates, ΣDEHP was highest in children and mothers (55.7/28.9μg/l). Compared to reference values derived from the German Human Biomonitoring Commission, children's 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 children's 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.
DINCH (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 μg/L in 2010 to twice the concentration in 2011 (0.31 μg/L) with further increases in 2013 (0.37 μg/L), 2015 (0.59 μg/L) and 2017 (0.70 μg/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 μg/L for the sum of OH-MINCH and cx-MINCH) or the tolerable daily intake (TDI) of EFSA (1 mg/kg bw/d). The median daily DINCH intake (DI) calculated for 2017 was 0.23 μg/kg bw/d, thus 4,310-times lower than the TDI. The maximum DI calculated for one individual in 2012 (42.60 μg/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.
Human biomonitoring studies measuring phthalate metabolites in urine have shown widespread exposure to phthalates in the general population. Diet is thought to be a principle route of exposure to ...many phthalates. Therefore, we studied urinary phthalate metabolite patterns over a period of strict fasting and additionally recorded personal activity patterns with a diary to investigate non-dietary routes of exposure. Five individuals (3 female, 2 male, 27–47 years of age) fasted on glass-bottled water only over a 48-h period. All urine void events were captured in full, and measured for metabolites of the high molecular weight (HMW) di-(2-ethylhexyl) phthalate (DEHP), di-isononyl phthalate (DINP) and di-isodecyl phthalate (DiDP), and the low molecular weight (LMW) di-n-butyl phthalate (DnBP), di-iso-butyl phthalate (DiBP), butylbenzyl phthalate (BBzP), dimethyl phthalate (DMP), and diethyl phthalate (DEP). In all, 21 metabolites were measured in a total of 118 urine events, including events before and after the fasting period. At the onset of the study all phthalate metabolite concentrations were consistent with levels found in previous general population studies. Metabolites of the HMW phthalates (DEHP, DiNP and DiDP) showed a rapid decline to levels 5–10 times lower than initial levels within 24h of the fast and remained low thereafter. After food consumption resumed, levels rose again. By contrast, metabolites of the LMW phthalates including DMP, DEP, BBzP, DnBP and DiBP showed a cyclical pattern of rising and declining concentrations suggestive of ongoing non-food exposures. Furthermore, metabolites of most of the LMW phthalates (BBzP, DnBP and DiBP) tracked each other remarkably well, suggesting concurrent exposures. Diary entries could not help explain exposure sources for these phthalates, with one exception: rises in MEP concentrations around males’ showers suggest personal care products as a major source of DEP. Exposure to HMW phthalates in this cohort appears to be driven by dietary intake, while non-dietary routes such as use of personal care products and ubiquitous sources including dust and indoor air appear to explain exposure to LMW phthalates.
Bisphenol A (BPA) exposure during early life may have endocrine-disrupting effects, but the dietary and sociodemographic predictors of BPA exposure during pregnancy and childhood remain unclear. Our ...aim was to evaluate the correlations between, and sociodemographic and dietary predictors of, serial urinary BPA concentrations measured during pregnancy and childhood in a Spanish birth cohort study. BPA was measured in two spot urine samples collected from 479 women during the first and third trimester of pregnancy and in one urine sample from their 4-year old children (n=130). Average dietary intakes were reported in food frequency questionnaires during the first and third pregnancy trimester and at age 4years. Multivariate mixed models and linear regression models were used to estimate associations between sociodemographic and dietary factors and BPA concentrations. A small, but statistically significant correlation was found between serial maternal BPA concentrations measured during pregnancy (r=0.17). Pregnant women who were younger, less-educated, smoked, and who were exposed to second-hand tobacco smoke (SHS) had higher BPA concentrations than others. BPA concentrations were also higher in children exposed to SHS. High consumption of canned fish during pregnancy was associated with 21% GM ratio=1.21; 95%CI 1.02, 1.44 and 25% GM ratio=1.25; 95%CI 1.05, 1.49 higher urinary BPA concentrations in the first and third pregnancy trimester, respectively, compared to the lowest consumption group. This study suggests that canned fish may be a major source of BPA during pregnancy in Spain, a country of high canned fish consumption. Further evaluation of specific BPA exposure sources in the sociodemographic group of younger women who smoke, are exposed to SHS, and have a low educational level is needed. Studies identifying sources of exposure would benefit from repeat BPA measurements and questionnaires specifically focused on dietary and packaging sources.
•Very weak correlations exist between serial BPA measurements during pregnancy.•Canned tuna may be a major source of BPA in mothers and children in Spain.•Prenatal BPA levels were higher in younger mothers who smoke, and are less-educated.•Future studies need more specific questions on diet and packaging sources.
Few human data on exposure and toxicity are available on neonicotinoids and neonicotinoid-like compounds (NNIs), an important group of insecticides worldwide. Specifically, exposure assessment of ...humans by biomonitoring remains a challenge due to the lack of appropriate biomarkers. We investigated the human metabolism and metabolite excretion in urine of acetamiprid (ACE), clothianidin (CLO), flupyradifurone (FLUP), imidacloprid (IMI), sulfoxaflor (SULF), thiacloprid (THIAC) and thiamethoxam (THIAM) after single oral dosages at the currently acceptable daily intake levels of the European Food Safety Authority. Consecutive post-dose urine samples were collected up to 48 h. Suspect screening of tentative metabolites was carried out by liquid chromatography–high-resolution mass spectrometry. Screening hits were identified based on their accurate mass, isotope signal masses and ratios, product ion spectra, and excretion kinetics. We found, with the exception of SULF, extensive metabolization of NNIs to specific metabolites which were excreted next to the parent compounds. Overall, 24 metabolites were detected with signal intensities indicative of high metabolic relevance. Phase-I metabolites were predominantly derived by mono-oxidation (such as hydroxy-FLUP, -IMI, and -THIAC) and by oxidative
N
-desalkylation (such as
N
-desdifluoroethyl-FLUP and
N
-desmethyl-ACE, -CLO and -THIAM). IMI-olefin, obtained by dehydration of hydroxylated IMI, was identified as a major metabolite of IMI. SULF was excreted unchanged in urine. Previously reported metabolites of NNIs such as 6-chloronicotinic acid or 2-chlorothiazole-4-carboxylic acid and their glycine derivatives were detected either at low signal intensities or not at all and seem less relevant for human biomonitoring. Our highly controlled approach provides specific insight into the human metabolism of NNIs and suggests suitable biomarkers for future exposure assessment at environmentally relevant exposures.
The grey matter is a central target of pathological processes in neurodegenerative disorders such as Parkinson's and Alzheimer's diseases. The grey matter is often also affected in multiple ...sclerosis, an autoimmune disease of the central nervous system. The mechanisms that underlie grey matter inflammation and degeneration in multiple sclerosis are not well understood. Here we show that, in Lewis rats, T cells directed against the neuronal protein β-synuclein specifically invade the grey matter and that this is accompanied by the presentation of multifaceted clinical disease. The expression pattern of β-synuclein induces the local activation of these T cells and, therefore, determined inflammatory priming of the tissue and targeted recruitment of immune cells. The resulting inflammation led to significant changes in the grey matter, which ranged from gliosis and neuronal destruction to brain atrophy. In humans, β-synuclein-specific T cells were enriched in patients with chronic-progressive multiple sclerosis. These findings reveal a previously unrecognized role of β-synuclein in provoking T-cell-mediated pathology of the central nervous system.
•Human urinary excretion kinetics of di(2-ethylhexyl) adipate (DEHA) after oral dose.•New specific DEHA metabolite: mono-5-carboxy-2-ethylpentyl adipate (5cx-MEPA).•Urinary excretion fractions (FUE) ...for three specific DEHA metabolites.•Calculation of metabolite-based daily DEHA intakes for pilot populations.•Highest FUE and detection rates for 5cx-MEPA.
Di(2-ethylhexyl) adipate (DEHA) is used as a substitute for the reprotoxic phthalate plasticizer di(2-ethylhexyl) phthalate (DEHP). This study reports the first quantitative data on human in vivo DEHA metabolism and urinary metabolite excretion with the aim of providing tools for DEHA exposure and risk assessments. After DEHA was administered to four healthy volunteers (107−164 μg/kg body weight (bw)), urine samples were continuously and completely collected for 48 h and analyzed for the specific oxidized monoester metabolites mono-2-ethyl-5-hydroxyhexyl adipate (5OH-MEHA), mono-2-ethyl-5-oxohexyl adipate (5oxo-MEHA), and mono-5-carboxy-2-ethylpentyl adipate (5cx-MEPA), as well as for the non-specific hydrolysis product adipic acid (AA) using stable isotope dilution analysis. AA was confirmed as a major (urinary excretion fraction (FUE): 10–40%), yet non-specific DEHA metabolite. 5cx-MEPA was the major specific DEHA metabolite with an FUE of 0.20% (range: 0.17–0.24%). FUEs for 5OH-MEHA and 5oxo-MEHA were 0.07% (0.03–0.10%) and 0.05% (0.01–0.06%), respectively. The three specific metabolites were excreted with two concentration maxima (tmax1 = 1.5–2.3 h, tmax2 = 3.8–6.4 h). Elimination half-lives (t1/2, calculated after the second tmax) for 5cx-MEPA were calculated between 2.1–3.8 h. The majority (98–100%) of metabolites was excreted within 24 h. The FUE of 5cx-MEPA was applied to demonstrate its applicability for calculating daily intakes based on urinary metabolite levels from three pilot populations. Daily intakes were generally far below the tolerable daily intake (TDI) for DEHA (300 μg/kg bw/day). The highest daily intake (114 μg/kg bw/day) was calculated in individuals after consuming food that had been wrapped in DEHA containing cling film.
Human biomonitoring studies measuring phthalate metabolites in urine have shown widespread exposure to phthalates in the general population. Diet is thought to be a principle route of exposure to ...many phthalates. Therefore, we studied urinary phthalate metabolite patterns over a period of strict fasting and additionally recorded personal activity patterns with a diary to investigate non-dietary routes of exposure. Five individuals (3 female, 2 male, 27-47 years of age) fasted on glass-bottled water only over a 48-h period. All urine void events were captured in full, and measured for metabolites of the high molecular weight (HMW) di-(2-ethylhexyl) phthalate (DEHP), di-isononyl phthalate (DINP) and di-isodecyl phthalate (DiDP), and the low molecular weight (LMW) di-n-butyl phthalate (DnBP), di-iso-butyl phthalate (DiBP), butylbenzyl phthalate (BBzP), dimethyl phthalate (DMP), and diethyl phthalate (DEP). In all, 21 metabolites were measured in a total of 118 urine events, including events before and after the fasting period. At the onset of the study all phthalate metabolite concentrations were consistent with levels found in previous general population studies. Metabolites of the HMW phthalates (DEHP, DiNP and DiDP) showed a rapid decline to levels 5-10 times lower than initial levels within 24 h of the fast and remained low thereafter. After food consumption resumed, levels rose again. By contrast, metabolites of the LMW phthalates including DMP, DEP, BBzP, DnBP and DiBP showed a cyclical pattern of rising and declining concentrations suggestive of ongoing non-food exposures. Furthermore, metabolites of most of the LMW phthalates (BBzP, DnBP and DiBP) tracked each other remarkably well, suggesting concurrent exposures. Diary entries could not help explain exposure sources for these phthalates, with one exception: rises in MEP concentrations around males' showers suggest personal care products as a major source of DEP. Exposure to HMW phthalates in this cohort appears to be driven by dietary intake, while non-dietary routes such as use of personal care products and ubiquitous sources including dust and indoor air appear to explain exposure to LMW phthalates.
Human exposure to Bisphenol A (BPA) is omnipresent. Both the extent of the exposure and its toxicological relevance are controversially discussed. We aim to reliably determine and evaluate the extent ...of BPA body burden in the German population from 1995 to 2009 based on 600 24 h urine samples and corresponding plasma samples from the Environmental Specimen Bank. We determined total and unconjugated BPA in urine and plasma using on-line solid-phase extraction high-performance liquid chromatography coupled to isotope dilution tandem mass spectrometry with a limit of quantification (LOQ) of 0.1 μg/l. In the stored urines, total BPA was quantifiable in >96% (median: 1.49 μg/l; 95th percentile: 7.37 μg/l), whereas unconjugated BPA was quantifiable only in <15% of the samples. Total BPA concentrations decreased over time, but 24 h urine volumes increased. Therefore, daily intakes calculated from the 24 h urines remained rather constant at a median of 0.037 and a 95th percentile of 0.171 μg BPA/kg body weight/day. In 60 corresponding plasma samples, total BPA levels were generally below the LOQ of 0.1 μg/l and, if quantifiable, most BPA was unconjugated, thus hinting to external contamination. We see total BPA in urine as the most appropriate and robust marker for BPA exposure assessment (if controlled for BPA contamination). Unconjugated BPA in urine and unconjugated or total BPA in plasma where contamination or breakdown of the glucuronide cannot be ruled out are of no value for human exposure assessment.
•Worldwide first representative data on exposure to NMP and NEP on national level.•Metabolites of NMP were found in 100%, NEP in 87% of all urine samples.•Higher NEP exposure of participants with low ...SES or migration background.
N-methyl-2-pyrrolidone (NMP) and its substitute N-ethyl-2-pyrrolidone (NEP) are aprotic solvents used in many technical applications, but also in carpets, and consumer products such as cleaning agents, and cosmetics. NMP and NEP are classified as reproductive toxicants. As a substance of very high concern (SVHC), NMP is included in the European REACH (Registration, Evaluation, Authorisation of Chemicals) candidate listfor authorisation. NMP and NEP metabolites were measured in more than 2100 urine samples of 3- to 17-year-old children and adolescents, participating in the population-representative German Environmental Survey for Children and Adolescents 2014–2017 (GerESV). The two NMP metabolites 5-hydroxy-N-methyl-2-pyrrolidone (5-HNMP) and 2-hydroxy-N-methylsuccinimide (2-HMSI) could be detected and quantified in all urine samples, and the two NEP metabolites 5-hydroxy-N-ethylpyrrolidone (5-HNEP) and 2-hydroxy-N-ethylsuccinimide (2-HESI) in 32% and 87% of the urine samples. Geometric mean concentrations were 103.1 µg/L (88.21 µg/gcreatinine) for the sum of NMP metabolites and 11.86 µg/L (10.15 µg/gcreatinine) for the sum of NEP metabolites, thus remaining below the current health-based human biomonitoring values.
For NMP, highest exposure was found in young children, but exposure pathways could not be revealed. Exposure to NEP was highest in adolescents and participants with low socio-economic status or migration background. Associations to usage of personal care products suggested the choice of products to have a distinct impact on NEP exposure.
The presented data can be used by the German Human Biomonitoring Commission to derive new reference values (RV95) for NMP and NEP for children and adolescents in Germany. This will facilitate to recognise changing exposure levels in this population group in Germany.
PDF
