Kinetics of di(2-ethylhexyl) phthalate (DEHP) and mono(2-ethylhexyl) phthalate in blood and of DEHP metabolites in urine of male volunteers after single ingestion of ring-deuterated DEHP (original) (raw)
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Toxicology Letters, 2018
Di-(2-propylheptyl) phthalate (DPHP) is used as a plasticizer for polyvinyl chloride products. A tolerable daily intake of DPHP of 0.2 mg/kg body weight has been derived from rat data. Because toxicokinetic data of DPHP in humans were not available, it was the aim of the present work to monitor DPHP and selected metabolites in blood and urine of 6 male volunteers over time following ingestion of a single DPHP dose (0.7 mg/kg body weight). Concentration-time courses in blood were obtained up to 24 h for DPHP, mono-(2-propylheptyl) phthalate (MPHP), mono-(2-propyl-6-hydroxyheptyl) phthalate (OH-MPHP), and mono-(2-propyl-6-oxoheptyl) phthalate (oxo-MPHP); amounts excreted in urine were determined up to 46 h for MPHP, OH-MPHP, oxo-MPHP, and mono-(2-propyl-6-carboxyhexyl) phthalate (cx-MPHP). All curves were characterized by an invasion and an elimination phase the kinetic parameters of which were determined together with the areas under the concentration-time curves in blood (AUCs). AUCs were: DPHP > MPHP > oxo-MPHP > OH-MPHP. The amounts excreted in urine were: oxo-MPHP > OH-MPHP > > cx-MPHP > MPHP. The AUCs of MPHP, oxo-MPHP, or OH-MPHP could be estimated well from the cumulative amounts of urinary OH-MPHP or oxo-MPHP excreted within 22 h after DPHP intake. Not considering possible differences in species-sensitivity towards unconjugated DPHP metabolites, it was concluded from a comparison of their AUCs in DPHP-exposed humans with corresponding earlier data in rats that there is no increased risk of adverse effects associated with the internal exposure of unconjugated DPHP metabolites in humans as compared to rats when receiving the same dose of DPHP per kg body weight.
Toxicology Letters, 2016
Di-(2-propylheptyl) phthalate (DPHP) does not act as a reproductive toxicant or endocrine disruptor in contrast to other phthalates. Considering adverse effects of phthalates to be linked to their metabolism, it was the aim of the present study to investigate in the rat the blood burden of DPHP and its metabolites as a basis for understanding the toxicological behavior of DPHP. Rats were administered single oral doses of DPHP of 0.7 and 100 mg/kg body weight. Concentration-time courses of DPHP and metabolites were monitored in blood. The areas under the concentration-time curves in blood (AUCs), normalized for the dose of DPHP, showed the following order: DPHP < mono-(2-propyl-6-oxoheptyl) phthalate < mono-(2-propyl-6-hydroxyheptyl) phthalate = mono-(2-propylheptyl) phthalate < mono-(2propyl-6-carboxyhexyl) phthalate (cx-MPHP). Glucuronidation of the monoesters accounted for less than 5% of total compounds. The elimination half-lives of the compounds ranged from 2.3 h (DPHP) to 8.2 h (cx-MPHP). The normalized AUCs of the metabolites were lower at the high dose of DPHP than at the low one indicating saturation kinetics of intestinal DPHP hydrolysis. The absence of toxicity to reproduction of DPHP may be related to the comparatively low bioavailability of the parent compound and its metabolites. Abbreviations AUC, concentration-time curve in blood calculated for t→∞; b.w., body weight; cx-MPHP(-d4), non-or ring-deuterated mono-(2-propyl-6-carboxyhexyl) phthalate; cx-MPHP, mono-(2-propyl-6-carboxyhexyl) phthalate; cx-MPHP-d4, ring-deuterated mono-(2-propyl-6-carboxyhexyl) phthalate; DEHP, di-(2-ethylhexyl) phthalate; DINP, di-isononyl phthalate; DPHP(-d4), non-or ring-deuterated di-(2-propylheptyl) 3 phthalate; DPHP, di-(2-propylheptyl) phthalate; DPHP-d4, ring-deuterated di-(2propylheptyl) phthalate; MEHP, mono-(2-ethylhexyl) phthalate; MPHP(-d4), non-or ring-deuterated mono-(2-propylheptyl) phthalate; MPHP, mono-(2-propylheptyl) phthalate; MPHP-d4, ring-deuterated mono-(2-propylheptyl) phthalate; OH-MPHP(-d4), non-or ring-deuterated mono-(2-propyl-6-hydroxyheptyl) phthalate; OH-MPHP, mono-(2-propyl-6-hydroxyheptyl) phthalate; OH-MPHP-d4, ring-deuterated mono-(2propyl-6-hydroxyheptyl) phthalate; oxo-MPHP(-d4), non-or ring-deuterated mono-(2propyl-6-oxoheptyl) phthalate; oxo-MPHP, mono-(2-propyl-6-oxoheptyl) phthalate; oxo-MPHP-d4, ring-deuterated mono-(2-propyl-6-oxoheptyl) phthalate; t1/2, half-life of the elimination phase
Metabolite Profiles of Di-n-butyl Phthalate in Humans and Rats
Environmental Science & Technology, 2007
Din -butyl phthalate (DBP) is widely used in consumer products. In humans and in rats, DBP is metabolized to monon-butyl phthalate (MBP). MBP may also further oxidize to other metabolites of DBP. We studied the metabolic profiles of DBP in rats and humans to evaluate the similarities between the two species and between different exposure scenarios. In rats administered DBP by oral gavage, we identified MBP and three urinary oxidative metabolites of DBP: mono-3-oxo-n-butyl phthalate, mono-3-hydroxyn-butyl phthalate (MHBP), and mono-3-carboxypropyl phthalate (MCPP). MBP, MHBP, and MCPP were also present in serum, albeit at lower levels than in urine. Statistically significant correlations (p < 0.01) existed between the concentrations of MBP and the concentrations of MHBP (Pearson correlation coefficient r) 0.82 [urine] and r) 0.96 [serum]) and MCPP (r) 0.77 [urine] and r) 0.97 [serum]). However, the concentrations of these metabolites in urine collected 6 h after dosing and in serum 24 h after dosing were not correlated, suggesting continuous metabolism of DBP and/or individual differences among rats. Serum DBP metabolite concentrations increased with the dose, whereas urinary concentrations did not. We also identified MBP, MHBP, and MCPP in the urine of four men exposed to DBP by taking a prescription medication containing DBP, and MBP and MCPP in 94 adults with no documented exposure to DBP. In the human samples, we observed statistically significant correlations (p < 0.01) among the urinary concentrations of MBP and MCPP, although the correlation was stronger for the four exposed men (r) 0.99) than for the adults without a documented exposure to DBP (r) 0.70). Our results suggest that regardless of species and exposure scenario, MBP, the major DBP metabolite, is an optimal biomarker of exposure to DBP. In addition to MBP, MCPP and MHBP may be adequate biomarkers of exposure to DBP in occupational settings or in potential high-exposure scenarios.
Toxicology Letters, 2001
The effects of phthalate esters of branched chain alcohols, typified by di-(2-ethylhexyl)phthalate (DEHP) differ from those of esters of straight chain alcohols typified by di-n-hexyl phthalate (DnHP). The former induce liver enlargement and proliferation of hepatic peroxisomes, while the latter cause no peroxisome proliferation but cause fat accumulation in the liver. Both classes of phthalate esters are hypolipidaemic and cause thyroid changes associated with an increased rate of thyroglobulin turnover. As phthalate esters are used as mixtures, we have examined the effect of mixtures of the compounds. Groups of five male Wistar albino rats were administered either control diet or diets containing either 10 000 ppm of DEHP, 10 000 ppm of DnHP or 10 000 ppm DEHP plus 10 000 ppm DnHP for 14 days. Rats receiving diets containing DEHP showed the expected increase in relative liver weight, in ''peroxisomal'' fatty acid oxidation and in CYP4A1. Serum triglyceride and serum cholesterol were also reduced, and the thyroid showed the histological changes mentioned above. Rats consuming diets containing DnHP showed no increase in relative liver weight and no induction of peroxisomal fatty acid oxidation or CYP4A1. However, there was a marked accumulation of fat in the liver. The fall in serum cholesterol was similar to that in rats treated with DEHP, but the fall of serum triglyceride was more pronounced. Thyroidal changes were again observed. In general, changes in rats treated with a mixture of DEHP and DnHP were very similar to those found with rats treated with DEHP alone. The liver was enlarged, and peroxisomal fatty acid oxidation and CYP4A1 were both induced. The amount of fat in the liver was much less than in rats receiving DnHP alone. Thyroid changes were similar to those in rats receiving the individual compounds. The effect on serum cholesterol seemed additive, but the levels of serum triglyceride were intermediate between the groups receiving the single compounds.
Urinary and serum metabolites of di-n-pentyl phthalate in rats
Chemosphere, 2011
Din -pentyl phthalate (DPP) is used mainly as a plasticizer in nitrocellulose. At high doses, DPP acts as a potent testicular toxicant in rats. We administered a single oral dose of 500 mg kg À1 bw of DPP to adult female Sprague-Dawley rats (N = 9) and collected 24-h urine samples 1 d before and 24-and 48-h after DPP was administered to tentatively identify DPP metabolites that could be used as exposure biomarkers. At necropsy, 48 h after dosing, we also collected serum. The metabolites were extracted from urine or serum, resolved with high performance liquid chromatography, and detected by mass spectrometry. Two DPP metabolites, phthalic acid (PA) and mono(3-carboxypropyl) phthalate (MCPP), were identified by using authentic standards, whereas mono-n-pentyl phthalate (MPP), mono(4-oxopentyl) phthalate (MOPP), mono(4-hydroxypentyl) phthalate (MHPP), mono(4-carboxybutyl) phthalate (MCBP), mono(2carboxyethyl) phthalate (MCEP), and mono-n-pentenyl phthalate (MPeP) were identified based on their full scan mass spectrometric fragmentation pattern. The x À 1 oxidation product, MHPP, was the predominant urinary metabolite of DPP. The median urinary concentrations (lg mL À1) of the metabolites in the first 24 h urine collection after DPP administration were 993 (MHPP), 168 (MCBP), 0.2 (MCEP), 222 (MPP), 47 (MOPP), 26 (PA), 16 (MPeP), and 9 (MCPP); the concentrations of metabolites in the second 24 h urine collection after DPP administration were significantly lower than in the first collection. We identified some urinary metabolic products in the serum, but at much lower levels than in urine. Because of the similarities in metabolism of phthalates between rats and humans, based on our results and the fact that MHPP can only be formed from the metabolism of DPP, MHPP would be the most adequate DPP exposure biomarker for human exposure assessment. Nonetheless, based on the urinary levels of MHPP, our preliminary data suggest that human exposure to DPP in the United States is rather limited.
Urinary oxidative metabolites of di(2-ethylhexyl) phthalate in humans
Toxicology, 2006
Di(2-ethylhexyl) phthalate (DEHP) is added to polyvinyl chloride (PVC) plastics used widely in medical devices and toys to impart flexibility and durability. DEHP produces reproductive and development toxicities in rodents. Initial metabolism of DEHP in animals and humans results in mono(2-ethylhexyl) phthalate (MEHP), which subsequently metabolizes to a wide range of oxidative metabolites before being excreted in urine and feces. We investigated the metabolism of DEHP in humans by identifying urinary oxidative metabolites of DEHP from individuals with urinary MEHP concentrations about 100 times higher than the median concentration in the general US population. In addition to the previously identified DEHP metabolites MEHP, mono(2-ethyl-5-oxohexyl) phthalate (MEOHP), mono(2-ethyl-5-hydroxyhexyl) phthalate (MEHHP), mono(2-ethyl-5-carboxypentyl) phthalate (MECPP), and mono(2-carboxymethylhexyl) phthalate (MCMHP), we also identified for the first time in humans three additional oxidative metabolites, mono(2-ethyl-3-carboxypropyl) phthalate (MECPrP), mono(2-ethyl-4-carboxybutyl) phthalate (MECBP), and mono(2-(1-oxoethyl)hexyl) phthalate (MOEHP) based on their chromatographic behavior and mass spectrometric fragmentation patterns. We also tentatively identified metabolites with two functional groups in the side alkyl chain as isomers of mono(2hydroxyethyl-4-carboxybutyl) phthalate (MHECBP), mono(2-ethyl-4-oxo-5-carboxypentyl) phthalate (MEOCPP), and mono(2ethyl-4-hydroxy-5-carboxypentyl) phthalate (MEHCPP). We report the presence of urinary DEHP metabolites in humans that have fewer than eight carbons in the alkyl chain. These metabolites were previously identified in rodents. Although quantitative information is not available, our findings suggest that, despite potential differences among species, the oxidative metabolism of DEHP in humans and rodents results in similar urinary metabolic products.
Urinary metabolites of diisodecyl phthalate in rats
Toxicology, 2007
Diisodecyl phthalate (DiDP) is an isomeric mixture of phthalates with predominantly 10-carbon branched-dialkyl chains, widely used as a plasticizer for polyvinyl chloride. The extent of human exposure to DiDP is unknown in part because adequate biomarkers of exposure to DiDP are not available. We identified several major metabolites of DiDP in urine of adult female Sprague-Dawley rats after a single oral administration of DiDP (300 mg/kg). These metabolites can potentially be used as biomarkers of exposure to DiDP. The metabolites extracted from urine were chromatographically resolved and identified by their chromatographic behavior and full scan negative ion electrospray ionization mass spectrum. The identity of metabolites with similar molecular weights was further examined in accurate mass mode. For some metabolites, unequivocal identification was done using authentic standards. Among these were the hydrolytic monoester of DiDP, monoisodecyl phthalate (MiDP), detected as a minor metabolite, and one oxidation product of MiDP, mono(carboxy-isononyl) phthalate (MCiNP), which was the most abundant urinary metabolite. We also tentatively identified other secondary metabolites of MiDP, mono(hydroxy-isodecyl) phthalate, mono(oxo-isodecyl) phthalate, mono(carboxyisoheptyl) phthalate, mono(carboxy-isohexyl) phthalate, mono(carboxy-isopentyl) phthalate, mono(carboxy-isobutyl) phthalate, and mono(carboxy-ethyl) phthalate. Oxidative metabolites of diisoundecyl phthalate (DiUdP) and diisononyl phthalate (DiNP) were also detected suggesting the presence of DiUdP and DiNP in the DiDP formulation. The urinary concentrations of all these metabolites gradually decreased in the 4 days following the administration of DiDP. MCiNP and other DiDP secondary metabolites are more abundant in urine than MiDP, suggesting that these oxidative products are better biomarkers for DiDP exposure assessment than MiDP. Additional research on the toxicokinetics of these metabolites is needed to understand the extent of human exposure to DiDP from the urinary concentrations of MCiNP and other DiDP secondary metabolites.
Food and Chemical Toxicology, 2011
This study has obtained estimates of the kinetics and fractional excretion factors of metabolism of DEHP and DINP to their main primary and secondary metabolites. Samples were obtained from an open-label, fixed sequence, single oral dose study in 10 male and 10 female subjects. The dosed substances were deuterated di-2-ethylhexylphthalate (D 4 -DEHP) and di-isononylphthalate (D 4 -DINP) at two dose levels. Urine samples were collected at intervals up to 48 h post-dose. LC-MS/MS was used to measure metabolite concentrations. Excreted amounts were then calculated using urine volumes. Metabolite half-lives were estimated to be 4-8 h with more than 90% of metabolites in the first 24 h of urine collections and the remainder in the 24-48 h period. The four metabolites of DEHP amounted to 47.1 ± 8.5% fractional excretion on a molar basis. For DINP the identified metabolites totalled 32.9 ± 6.4%. For both DEHP and DINP the metabolites were in the abundance order -monoester < -oxo < -carboxy < -hydroxy. These robust fractional excretion values for the main primary and secondary phthalate metabolites along with estimates of their uncertainty can be used in future surveys of human exposure to DEHP and DINP.