Hans Drexler

An estimation of the daily intake of di(2-ethylhexyl)phthalate (DEHP) and other phthalates in the general population.

We analyzed 85 urine samples of the general German population for human specific metabolites of phthalates. By that we avoided contamination with the parent phthalates being omnipresent in the environment and for the first time could deduce each individuals internal exposure to phthalates without contamination. Determined were the secondary metabolites mono(2-ethyl-5-hydroxyhexyl)phthalate (5OH-MEHP) and mono(2-ethyl-5-oxo-hexyl)phthalate (5oxo-MEHP) of di(2-ethylhexyl)phthalate (DEHP) and the primary monoester metabolites of DEHP, di-noctylphthalate (DnOP), di-n-butylphthalate (DnBP), butylbenzylphthalate (BBzP) and diethylphthalate (DEP). Based on these internal exposure values we calculated the daily intake of the parent phthalates using urinary metabolite excretion factors. For DEHP we determined a median intake of 13.8 micrograms/kg body weight/day and an intake at the 95th percentile of 52.1 micrograms/kg body weight/day. The tolerable daily intake (TDI) value settled by the EU Scientific Committee for Toxicity, Ecotoxicity and the Environment (CSTEE) is 37 micrograms/kg body weight/day. Twelve percent of the subjects (10 out of 85 samples) within our collective of the general population are exceeding this value. Thirty-one percent of the subjects (26 out of 85 samples) had values higher than the reference dose (RfD) of 20 micrograms/kg body weight/day of the U.S. Environmental Protection Agency (EPA). For DnBP, BBzP, DEP and DnOP intake values at the 95th percentile were 16.2, 2.5, 22.1 and 0.42 micrograms/kg body weight/day respectively. Our results unequivocally prove that the general German population is exposed to DEHP to a much higher extent than previously believed. This is of greatest importance for public health since DEHP is not only the most important phthalate with respect to its production, use, occurrence and omnipresence but also the phthalate with the greatest endocrine disrupting potency. DEHP is strongly suspected to be a developmental and reproductive toxicant. We are not aware of any other environmental contaminant for which the TDI and RfD are exceeded to such an extent within the general population. The transgressions of the TDI and RfD for DEHP are accompanied by considerable ubiquitous exposures to DnBP and BbzP, two phthalates under scrutiny for similar toxicological mechanisms.

Internal exposure of the general population to DEHP and other phthalates—determination of secondary and primary phthalate monoester metabolites in urine☆

A number of phthalates and their metabolites are suspected of having teratogenic and endocrine disrupting effects. Especially the developmental and reproductive effects of di(2-ethylhexyl)phthalate (DEHP) are under scrutiny. In this study we determined the concentrations of the secondary, chain oxidized monoester metabolites of DEHP, mono(2-ethyl-5-hydroxyhexyl)phthalate (5OH-MEHP) and mono(2-ethyl-5-oxo-hexyl)phthalate (5oxo-MEHP) in urine samples from the general population. The utilization of the secondary metabolites minimized any risk of contamination by the ubiquitously present phthalate parent compounds. Included in the method were also the simple monoester metabolites of DEHP, dioctylphthalate (DOP), di-n-butylphthalate (DnBuP), butylbenzylphthalate (BBzP) and diethylphthalate (DEP). Automated sample preparation was performed applying a column switching liquid chromatography system enabling online extraction of the urine on a restricted access material (RAM) and separation on a reversed phase analytical column. Detection was performed by negative ESI-tandem mass spectrometry in multiple reaction monitoring mode and quantification by isotope dilution. The excretion of DEHP and the other phthalates was studied by analyzing first morning urine samples from 53 women and 32 men aged 7-64 years (median: 34.2 years) living in northern Bavaria (Germany) who were not occupationally exposed to phthalates. Phthalate metabolites, secondary and primary ones, were detected in all specimens. Concentrations were found to vary strongly from phthalate to phthalate and subject to subject with differences spanning more than three orders of magnitude. Median concentrations for excretion of DEHP metabolites were 46.8 microg/L for 5OH-MEHP (range 0.5-818 microg/L), 36.5 microg/L for 5oxo-MEHP (range 0.5-544 microg/L), and 10.3 microg/L for MEHP (range:<0.5 (limit of quantification, LOQ) to 177 microg/L). A strong correlation was found between the excretion of 5OH-MEHP and 5oxo-MEHP with a correlation coefficient of r=0.991, indicating close metabolic proximity of those two parameters but also the absence of any contaminating interference. Median concentrations for the other monoester metabolites were for mono-n-butylphthalate (MnBuP) 181 microg/L, for monobenzylphthalate (MBzP) 21.0 microg/L, for monoethylphthalate (MEP) 90.2 microg/L and for mono-n-octylphthalate (MOP)<1.0 microg/L (LOQ). These results will help to perform health risk assessments for the phthalate exposure of the general population.

Internal exposure of nursery-school children and their parents and teachers to di(2-ethylhexyl)phthalate (DEHP)

Di(2-ethylhexyl)phthalate (DEHP) is the main plasticizer for polyvinyl chloride (PVC) products. It has become widely spread in our environment and among people. DEHP is suspected to be responsible for endocrine-disruptor-like effects in mankind. Children are probably most susceptible to these endocrine effects. In this study we determined the internal exposure of nursery school children (aged 2-6 years) to DEHP and compared it to their parents and teachers exposure. The DEHP-metabolites mono(2-ethyl-5-hydroxyhexyl)phthalate (5OH-MEHP), mono(2-ethyl-5-oxo-hexyl)phthalate (5oxo-MEHP) and mono(2-ethylhexyl)phthalate (MEHP) were determined in first morning urine. The sum of the three DEHP metabolites in childrens and in adults urine was 90.0 and 59.1 micrograms/l respectively (median values; p = 0.074). Concentrations of the secondary metabolites 5OH-MEHP (median: 49.6 vs. 32.1 micrograms/l; p = 0.038) and 5oxo-MEHP (median: 33.8 vs. 19.6 micrograms/l; p = 0.015) were significantly higher in children than in adults. MEHP concentrations were low both in adults and children (median: 6.6 micrograms/l vs. 9.0 micrograms/l). Creatinine adjusted values should more accurately reflect the dose taken up with respect to body weight when comparing children with adults. Total creatinine adjusted DEHP metabolites in urine were significantly higher in children than in adults (median values: 98.8 vs. 50.9 micrograms/g creatinine; p < 0.0001). This also applied to the concentrations of both secondary metabolites 5OH-MEHP (55.8 vs. 28.1 micrograms/g creatinine; p < 0.0001) and 5oxo-MEHP (38.3 vs. 17.2 micrograms/g creatinine; p < 0.0001). Creatinine corrected concentrations for the monoester MEHP in children and adults were very similar (8.7 vs. 8.6 micrograms/g creatinine; p = 0.908). Based on the sum of the three determined metabolites we estimated the DEHP dose (in microgram/kg body-weight) taken up by children to be about twice as high as the dose taken up by adults. Routes of the ubiquitous exposure to DEHP remain indistinct. In childrens urine the mean relative ratios of MEHP to 5OH-MEHP to 5oxo-MEHP were 1 to 7.1 to 4.9, in adults they were 1 to 3.4 to 2.1. This might indicate an enhanced oxidative metabolism in children. To date no information on the biological activity and toxicity of oxidative metabolites of DEHP is available. Since these are the major metabolites of DEHP toxicological data on these metabolites is urgently needed.

Pyrethroid exposure of the general population —is this due to diet?

Inhabitants (1177) of a residential area in Frankfurt/Main have been investigated with respect to internal exposure to pyrethroids. Biological monitoring revealed a body burden of pyrethroids. The 95th per thousand for the urinary metabolites of pyrethroids, such as permethrin and cypermethrin, cis and trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane-1-carboxylic acid (cis-DCCA and trans-DCCA), was determined to be 0.5 and 1.4 microg/l, respectively. 95th per thousand for cis-3-(2,2-dibromovinyl)-2,2-dimethylcyclopropane-1-carboxylic acid (DBCA), a specific metabolite of deltamethrin, and 4-fluoro-3-phenoxybenzoic acid (F-PBA), a metabolite of cyfluthrin, were 0.3 and 0.27 microg/l, respectively. The metabolic pattern found for these samples points out that pyrethroids are probably ingested orally with daily diet.

Determination of haemoglobin adducts of acrylamide and glycidamide in smoking and non-smoking persons of the general population

Acrylamide (AA) is a food-borne toxicant suspected to be carcinogenic to humans. It is formed in the heating process of starch-containing food. Currently, there is a great discussion about the possible human health risks connected with the dietary uptake of acrylamide. Haemoglobin adducts of acrylamide and its oxidative metabolite glycidamide are both markers of biochemical effect. However, because glycidamide has a higher carcinogenic potency than acrylamide itself, the glycidamide adduct might mirror the genotoxicity better than acrylamide adducts. In order to gain more information about the human metabolism of acrylamide, we investigated a small group of persons for the effective internal doses of acrylamide and glycidamide using haemoglobin adducts as parameters of biochemical effect. The collective was subdivided into non-smokers (n=13) and smokers (n=16) by determining the smoking-specific acrylonitrile haemoglobin adduct (N-cyanoethylvaline, CEV). The mean values for the adducts of acrylamide (N-2-carbamoylethylvaline, AAVal) and glycidamide (N-(R,S)-2-hydroxy-2-carbamoylethylvaline, GAVal) in nonsmokers was 19 pmol/g globin AAVal (range 7-31 pmol/g globin) and 17 pmol/g globin GAVal (range 9-23 pmol/g globin). For smokers mean levels of AAVal were 80 pmol/g globin (range: 25-199 pmol/g globin) and those of GAVal were 53 pmol/g globin (range: 22-119 pmol/g globin). Metabolism to glycidamide turned out to be significantly more effective in non-smokers than in the higher exposed smokers. Compared with studies in rats, the metabolic conversion of acrylamide to glycidamide as measured by haemoglobin adducts seems to occur to a similar extent in humans as in rats. Risk estimations on acrylamide based on experimental data obtained in rats obviously did not overestimate the cancer risk for the general population. Furthermore, our results might indicate that the dose-response curve for acrylamide is not linear. This would be in line with the results of animal experiments on rodents.

Hemoglobin adducts of ethylene oxide, propylene oxide, acrylonitrile and acrylamide -biomarkers in occupational and environmental medicine

In a chemical plant, ethylene oxide (EO) and propylene oxide (PO) were used for the production of surfactants for the textile industry. Within health supervision, we investigated the internal exposure of the workers using hemoglobin adducts as parameters of biochemical effects. The 95th percentile for N-2-hydroxyethylvaline (HEV) was 1280 pmol/g globin (=29.4 microg/l blood) in blood from exposed workers compared with 100 pmol/g globin (or 2.3 microg/l) in controls. N-(R,S)-2-hydroxypropylvaline (HPV) both in workers and controls was below the detection limit (80 pmol/g globin or 2 microg/l). The levels of the adducts of acrylonitrile (ACN) and acrylamide (AA) were also determined, though they were mainly accounted for by smoking and diet. Median values of N-2-cyanoethylvaline (CEV) were below 4 pmol/g globin (or 0.1 microg/l) in non-smokers (n=24) and 131 pmol/g globin (or 3.3 microg/l) in smokers (n=38). Median values of N-2-carbamoylethylvaline (AAV) were 22 pmol/g globin (or 0.6 microg/l) in non-smokers compared with 89 pmol/g globin (or 2.4 microg/l) in smokers. Correlations were found between smoking habits and adduct levels of CEV and AAV.

Evidence for increased internal exposure to lower chlorinated polychlorinated biphenyls (PCB) in pupils attending a contaminated school.

External and internal exposure to six WHO-indicator congeners of polychlorinated biphenyls (PCB 28, 52, 101, 138, 153, 180) as well as subjective health complaints of a group of 377 pupils attending a PCB-contaminated school were compared with a control group of 218 pupils attending a non-contaminated school. Indoor air of the contaminated school revealed total PCB concentrations (sum of six indicator congeners times 5) ranging between 690 and 20,800 ng/m3 (median 2044 ng/m3). The lower chlorinated congeners PCB 28, 52, 101 were the prevailing contaminants (median 33, 293, and 66 ng/m3). Using improved analytical procedures at least one of the lower chlorinated congeners could be detected in 95% of the blood samples of pupils attending the contaminated school. Median concentrations for PCB 28, 52, 101, and for the sum of lower chlorinated congeners were 6, 9, 5, and 22 ng/l blood plasma, respectively, whereas the corresponding values in the control group were all < 1 ng/l. In contrast, no significant differences were found for the higher chlorinated congeners (PCB 138, 153, 180) which were detected in 1-2 orders of magnitude higher concentrations in both groups. Due to the dietary intake of these congeners similar total PCB levels were found (95th percentile 1070 and 1010 ng/l plasma in participants of the contaminated and control school). Using the Giessen Subjective Complaint List for Children and Adolescents no statistically significant differences in health complaints were observed between both groups of children. It is concluded that exposure of pupils to PCB in indoor air of the contaminated school caused increased blood concentrations of lower chlorinated congeners. Compared to background levels the detected excess body burden was very low indicating no additional health risk. Exposure was not associated to any specific subjective complaints.

A first approach to estimate the internal exposure to acrylamide in smoking and non-smoking adults from Germany

Since the formation of acrylamide (AA) in the heating process of starch-containing food could be demonstrated and high contents of this substance were found in commercial food products, there is a great discussion about the possible human health risks connected with this dietary exposure. In order to determine the body burden of the general population in Germany caused by this uptake, we investigated the internal exposure to acrylamide and acrylonitrile in a group of 72 persons using haemoglobin adducts as parameters of biochemical effects. The collective was subdivided into non-smokers and smokers basing on the results of the smoking-specific acrylonitrile adduct (N-cyanoethylvaline, CEV). The median value for the adduct of AA (N-2-carbamoylethylvaline, AAV) in 25 non-smokers was 21 pmol/g globin (approximately 0.6 microgram/l blood) with a 95 percentile of 46 pmol/g globin (approximately 1.3 micrograms/l) (LOD: 12 pmol/g globin). The median level for AAV in smokers (n = 47) was found to be 85 pmol/g globin (approximately 2.3 micrograms/l blood) with a 95 percentile of 159 pmol/g globin (approximately 4.3 micrograms/l blood). Based on these results about 60 micrograms AA/d are taken up by adult non-smoking persons. According to calculations of WHO and US EPA this background exposure would lead to a cancer risk between 6 x 10(-4) and 3.6 x 10(-3). Our results confirm a body burden to AA even in persons from the non-smoking general population in Germany that is most probably caused by dietary uptake. Smoking habits considerably contribute to the level of this adduct.

Determination of six hydroxyalkyl mercapturic acids in human urine using hydrophilic interaction liquid chromatography with tandem mass spectrometry (HILIC–ESI-MS/MS) ☆

Mercapturic acids are increasingly used as biomarkers for exposure to certain carcinogenic substances. Glycidol, ethylene oxide, propylene oxide, acrolein and 1,3-butadiene are important intermediates of toxicological concern used in the industrial production of various chemicals. The main urinary metabolites of these alkylating substances are hydroxyalkyl mercapturic acids. Therefore, we developed and validated an analytical method for the simultaneous determination of six hydroxyalkyl mercapturic acids in human urine after solid phase extraction. The mercapturic acids were separated using hydrophilic interaction liquid chromatography (HILIC) and quantified by tandem mass spectrometry using isotopically labelled internal standards. The developed method enables for the first time the determination of 2,3-dihydroxypropyl mercapturic acid (DHPMA), a metabolite of glycidol, in human urine. Additionally, the mercapturic acids of ethylene oxide (hydroxyethyl mercapturic acid, HEMA), propylene oxide (2-hydroxypropyl mercapturic acid, 2-HPMA), acrolein (3-hydroxypropyl mercapturic acid, 3-HPMA) as well as of 1,3-butadiene(3,4-dihydroxybutyl mercapturic acid, DHBMA and monohydroxy-3-butenyl mercapturic acid, MHBMA) can be determined. The limits of detection range from 3.0 to 7.0 μg/L. Intra- and inter-day precision was determined to range from 1% to 9%. Due to the good accuracy and precision and the low limits of detection the developed method is well suited for the determination of occupational exposure to alkylating substances as well as for the determination of background concentrations of the respective mercapturic acids in the general population.

Mercapturic acids as metabolites of alkylating substances in urine samples of German inhabitants

Hydroxyalkyl mercapturic acids (HAMA) are the main urinary metabolites of several alkylating substances that possess a carcinogenic potential, like acrolein, 1,3-butadiene, ethylene oxide, propylene oxide and glycidol. These alkylating substances are used extensively in industrial processes, but they do also occur environmentally, e.g. in tobacco smoke. The aim of this study was the determination of six HAMA, as biomarkers of exposure, in human urine of smokers and non-smokers. We applied a sensitive analytical method, using hydrophilic interaction liquid chromatography with tandem mass spectrometry (HILIC-MS/MS) for the determination of 2-hydroxyethyl mercapturic acid (HEMA, biomarker for ethylene oxide), 2-hydroxypropyl mercapturic acid (2-HPMA, biomarker for propylene oxide), 3-hydroxypropyl mercapturic acid (3-HPMA, biomarker for acrolein), 2,3-dihydroxypropyl mercapturic acid (DHPMA, biomarker for glycidol) as well as 3,4-dihydroxybutyl mercapturic acid and 3-monohydroxybutenyl mercapturic acids (DHBMA and MHBMA, biomarkers for 1,3-butadiene). Background concentrations of four HAMA were detected in each urine sample we analyzed. The mercapturic acids HEMA and MHBMA were detected in 55% and 10% of the samples, respectively. In the urine of non-smokers (n = 54) we observed median levels of 206, 1.6, 12.1, 146, 159, and <5.0 μg/g creatinine for DHPMA, HEMA, 2-HPMA, 3-HPMA, DHBMA and MHBMA, respectively. Among smokers (n = 40) median levels of DHPMA, HEMA, 2-HPMA, 3-HPMA, DHBMA and MHBMA were determined to be 217, 4.9, 46.2, 884, 211 and <5.0 μg/g creatinine, respectively. The excretion rate of the biomarkers HEMA, 2-HPMA and 3-HPMA was distinctly higher in smokers than in non-smokers. Furthermore, our study revealed a comparatively high background level of DHPMA in urine of smokers and non-smokers whose origin is still unknown. The presented data may contribute to the evaluation of reference values for urinary HAMA levels in the general population.