Comparison of aggregated exposure to perfluorooctanoic acid (PFOA) from diet and personal care products with concentrations in blood using a PBPK model - Results from the Norwegian biomonitoring study in EuroMix.

BACKGROUND: Per- and polyfluoroalkyl substances (PFAS) constitute a large group of compounds that are water, stain, and oil repellent. Numerous sources contribute to the blood levels of PFAS in the European population. The main contributor for perfluorooctanoic acid (PFOA) is food, house dust, consumer products and personal care products (PCPs). OBJECTIVES: The purpose of the present work is to calculate the dietary and dermal external exposure to PFOA, estimate the aggregated internal exposure from diet and PCPs using a PBPK model, and compare estimates with measured concentrations. METHODS: Detailed information on diet and PCP use from the EuroMix study is combined with concentration data of PFOA in food and PCPs in a probabilistic exposure assessment. A physiologically based pharmacokinetic model (PBPK) was further refined by incorporating a dermal exposure pathway, and changes in the kidney and faecal excretion. RESULTS: The aggregated internal exposure using the PBPK model shows that the major contributor to the internal exposure is diet for both males and females. The estimated internal exposure of PFOA for the EuroMix population was in the same range but lower than the measured blood concentrations using the lower bound (LB) external exposure estimates, showing that the LB estimates are underestimations. For seven females the internal exposure of PFOA were higher from PCPs than from diet. CONCLUSION: PCPs and diet contributed in the same range to the internal PFOA exposure for several women participating in EuroMix. This calls for additional studies on exposure to PFOA and possibly other PFAS from PCPs, especially for women. Overall, PBPK modelling was shown as valuable tool in understanding the sources of PFOA exposure and in guiding risk assessments and regulatory decisions.

Per- and polyfluoroalkyl substances in serum and associations with food consumption and use of personal care products in the Norwegian biomonitoring study from the EU project EuroMix.

BACKGROUND: Human exposure to chemicals through the oral, dermal, or inhalation routes is significant. To assess this exposure, a human biomonitoring study was conducted in Norway to examine the plausibility of source-to-dose calculations for chemical mixtures. Per- and polyfluoroalkyl substances (PFASs) are man-made compounds used for their surfactant properties, and several are persistent and bioaccumulative. Some PFASs are toxic and are regarded as endocrine disruptors and have been shown to suppress immune function and affect cholesterol homeostasis. Using the participants from the EuroMix BM study, we set out to describe PFAS concentrations and to evaluate associations with diet and use of personal care products (PCPs). METHODS: Participants (44 males and 100 females) kept detailed diaries on their food consumption and their PCP use for two non-consecutive days. All urine (24 h) and blood samples were collected at the end of each study day. Levels of 25 PFASs were analysed in serum from study day 1 using a high throughput online solid phase extraction ultra-high-performance liquid chromatography tandem mass spectrometry method. Multivariable linear regressions were performed between each food and PCP category and each chemical and were sex-stratified when the consumption of food or use of PCPs was significantly different between men and women. RESULTS: Eight PFASs were detected in all analysed samples (PFHxS, PFHpS, PFOS, PFOA, PFNA, PFDA, PFUnDA and PFDoDA), and four PFASs were below the limit of detection (PFOPA, PFDPA, PFHxA, and EtFOSA). Several PFASs were found to be positively associated with fish consumption (PFOS, PFNA, PFUnDA, PFDoDA, PFDA, PFDS and PFTrDA). Sunscreen, mouthwash, and lip gloss/lip balm were found to be positively associated with PFASs (PFOA, PFTrDA, and PFOSA). CONCLUSION: The participants in the EuroMix study were exposed to PFASs through their diet and PCP use. Several foods and PCPs were found to be potential sources of exposure to PFASs.

Exposure estimates of phthalates and DINCH from foods and personal care products in comparison with biomonitoring data in 24-hour urine from the Norwegian EuroMix biomonitoring study.

Phthalates are diesters of phthalic acid and have been widely used as plasticizers in polyvinyl chloride (PVC) plastics. Phthalates are also used as excipients in pharmaceuticals and personal care products (PCPs). Phthalates can migrate from the plastic into the air, water and food, and humans can be exposed via multiple pathways such as dermal, oral and inhalation. There is evidence that phthalates can induce reproductive and developmental toxicity not only in experimental animals but also in humans through disruption of estrogenic activity. The aim of this study was to collect concentration data on five phthalates in foods and PCPs from the scientific literature and combine these with food consumption data and PCP use frequency data from the EuroMix biomonitoring (BM) study in order to assess exposure. Probabilistic exposure assessments of phthalates were performed from foods and PCPs. Due to the very limited data available in the literature for DINCH, an exposure assessment was not carried out for this compound. The food groups with the highest contribution to phthalates exposure were: beverages, dairy, bread and meat products. The exposure estimates were compared with the measured phthalate metabolite levels from 24-hour urine samples. Regarding the oral route, measured phthalate exposure was between the lower bound (LB) and medium bound (MB) estimated exposure for all phthalates, except for DEP. The measured exposure from urine correlated with the estimated exposure from food for DEHP and DBP, while for BBP and DEP it correlated with the exposure estimates from PCPs. There were no significant differences between the BM data and the estimated exposure, except for DINP for males (p = 0.01). The LB and MB phthalate exposures estimated from foods and PCPs and the measured exposure from the urine were considerably lower than their respective tolerable daily intake (TDI) values established by the European Food Safety Authority (EFSA) and the World Health Organization (WHO). For the upper bound (UB), the exposure estimates are approximately double the TDI; however, this is regarded as a worst-case estimate and has low correlation with the measured exposure.

Comparison of aggregated exposure to di(2-ethylhexyl) phthalate from diet and personal care products with urinary concentrations of metabolites using a PBPK model - Results from the Norwegian biomonitoring study in EuroMix.

Phthalates are widely used as plasticisers in flexible plastics and containers for food and personal care products (PCPs) and contaminates foods and PCPs. A human biomonitoring (BM) study was performed to study exposure of chemicals from foods and PCPs. For two 24-h periods, adult volunteers (n = 144) in Norway kept diaries on food eaten and usage of PCPs, and collected 24-h urine. Aggregated exposure to di(2-ethylhexyl) phthalate (DEHP) from dietary and PCPs was estimated by Monte-Carlo simulation using Oracle Crystal Ball©. Simulated urinary concentrations using physiologically based pharmacokinetic (PBPK) models were compared with measured urinary metabolites of DEHP, mono-2-ethylhexyl phthalate (MEHP), mono-2-ethyl-5-hydroxyhexyl phthalate (MEHHP), mono-2-ethyl-5-oxohexyl phthalate (MEOHP) and mono-2-ethyl 5-carboxypentyl phthalate (MECCP). DEHP exposure from food are approximately 10 times higher than exposure than from PCPs. The main contributors to dietary exposure are dairy, grain, fruits and vegetables, meat and fish. Body lotion contribute most to the exposure of DEHP from PCPs. Forward-dosimetry gives good convergence with 24-h urinary concentrations of simulated and measured BM data. The measured concentration of the MECCP metabolite correlated well with simulated high exposure, while the measured concentrations of MEHP, MEHHP and MEOHP partly overlapped with both simulated low, medium and high metabolite exposure.

Imaging considerations for in vivo 13C metabolic mapping using hyperpolarized 13C-pyruvate.

One of the challenges of optimizing signal-to-noise ratio (SNR) and image quality in (13)C metabolic imaging using hyperpolarized (13)C-pyruvate is associated with the different MR signal time-courses for pyruvate and its metabolic products, lactate and alanine. The impact of the acquisition time window, variation of flip angles, and order of phase encoding on SNR and image quality were evaluated in mathematical simulations and rat experiments, based on multishot fast chemical shift imaging (CSI) and three-dimensional echo-planar spectroscopic imaging (3DEPSI) sequences. The image timing was set to coincide with the peak production of lactate. The strategy of combining variable flip angles and centric phase encoding (cPE) improved image quality while retaining good SNR. In addition, two aspects of EPSI sampling strategies were explored: waveform design (flyback vs. symmetric EPSI) and spectral bandwidth (BW = 500 Hz vs. 267 Hz). Both symmetric EPSI and reduced BW trended toward increased SNR. The imaging strategies reported here can serve as guidance to other multishot spectroscopic imaging protocols for (13)C metabolic imaging applications.

The Norwegian biomonitoring study from the EU project EuroMix: Levels of phenols and phthalates in 24-hour urine samples and exposure sources from food and personal care products.

BACKGROUND: Exposure to multiple chemicals occurs daily through several routes; diet, inhalation and dermal contact. Real-life exposure assessment is needed to understand the risk. Therefore, a human biomonitoring (BM) study was performed to examine the plausibility of source-to-dose calculations for chemical mixtures in the Horizon 2020 EuroMix project. OBJECTIVES: To provide a detailed description of the design of the EuroMix BM study, and to present the initial results for urinary phenols and phthalates and to describe their exposure determinants from foods and personal care products (PCPs). METHOD: Adults (44 males and 100 females) kept detailed diaries on their food consumption, PCP use and handling of cash receipts. Urine samples were collected over the same 24-hour period. Urinary levels of four parabens, five bisphenols, oxybenzone/benzophenone-3 (OXBE), triclosan (TCS), triclocarban (TCC) and metabolites of eight phthalates and 1,2-cyclohexane dicarboxylic acid diisononyl ester (DINCH) were analysed by ultra-high-performance liquid chromatography and tandem mass spectrometry. Multivariable linear regressions were performed between PCPs/food categories and each dependent chemical variable separately, and were only sex-stratified when an interactions between sex and the independent variable was significant. RESULTS: The detection rate for the metabolites of phthalates and DINCH, and bisphenol A (BPA) and TCS in urine was 88-100%, while bisphenol S (BPS) and bisphenol F (BPF) were only found in 29% and 4% of the urine samples, respectively. Bisphenol B (BPB), bisphenol AF (BPAF) and TCC were not detected. Food groups associated with phenol exposure were meat, bread, beverages and butter and oil. Food determinants for phthalate exposure were sweets, butter and oil, fruit and berries and other foods. The only positive association between the use of PCPs and phenols was found between BPA and lip gloss/balm. Phthalate exposure was associated with the use of shower gel, hand cream (females), toothpaste, anti-wrinkle cream (females) and shaving products (males). CONCLUSION: The participants in the EuroMix BM study were exposed to a mixture of phenols and phthalates. A variety of food categories and PCPs were found to be possible sources of these chemicals. This indicates a complex pattern of exposure to numerous chemicals from multiple sources, depending on individual diet and PCP preferences.

Involvement of human glutathione S-transferase isoenzymes in the conjugation of cyclophosphamide metabolites with glutathione.

Alkylating agents can be detoxified by conjugation with glutathione (GSH). One of the physiological significances of this lies in the observation that cancer cells resistant to the cytotoxic effects of alkylating agents have higher levels of GSH and high glutathione S-transferase (GST) activity. However, little is known about the GSH-/GST-dependent biotransformation of alkylating agents, including cyclophosphamide. Cyclophosphamide becomes cytostatic after the enzymatic formation of 4-hydroxycyclophosphamide. The ultimate alkylating species formed from cyclophosphamide is phosphoramide mustard. In this paper we describe the involvement of purified human glutathione S-transferases isoenzymes GST A1-1, A2-2, M1a-1a, and P1-1 in the formation of two types of glutathionyl conjugates of cyclophosphamide, i.e., 4-glutathionylcyclophosphamide (4-GSCP) and monochloromonoglutathionylphosphoramide mustard. When 0.1 mM 4-hydroxycyclophosphamide and 1 mM GSH was incubated in the presence of 10 microM GST A1-1, A2-2, M1a-1a, and P1-1 the formation of 4-GSCP was 2-4-fold increased above the spontaneous level. Enzyme kinetic analysis demonstrated the lowest Km (0.35 mM) for GST A1-1. Km values for the other GST enzymes ranged from 1.0 to 1.9 mM. Glutathione S-transferase A1-1 (40 microM) also increased the conjugation of phosphoramide mustard and GSH (both 1 mM) 2-fold, while the other major human isoenzymes, A2-2, M1a-1a, and P1-1, did not influence the formation of monochloromonoglutathionylphosphoramide mustard. These results indicate that only one enzyme within the class of human GST alpha enzymes was able to catalyze the reaction of the aziridinium ion of phosphoramide mustard with glutathione. Thus increased levels of GST A1-1 in tumor cells can contribute to an enhanced detoxification of phosphoramide mustard and hence to the development of drug resistance. Since all of the human GSTs tested did catalyze the formation of 4-GSCP, the role of 4-GSCP either as a transport form of activated cyclophosphamide or as a detoxification product is discussed.

The role of human glutathione S-transferase isoenzymes in the formation of glutathione conjugates of the alkylating cytostatic drug thiotepa.

Nonenzymatic and glutathione S-transferase (GST) catalyzed glutathione (GSH) conjugation has been postulated as a mechanism by which alkylating cytostatic drugs can be inactivated intracellularly. In this study, we describe studies on the glutathione-dependent biotransformation of thiotepa (tris(1-aziridinyl)phosphine sulfide), a trifunctional alkylating agent. 31P NMR studies showed that thiotepa is stable in 0.07 M phosphate buffer, pH 7.4 (t1/2 = 3300 min). In the presence of glutathione, the rate of disappearance of thiotepa increased greatly (t1/2 = 282 min). Both monoglutathionyl thiotepa and diglutathionyl thiotepa conjugates were identified by 31P NMR and mass spectrometry. Addition of GST A1-1 (alpha) to an incubation of thiotepa and GSH further increased the rate of disappearance of thiotepa (t1/2 = 100 min) and increased the rate of formation of monoglutathionyl thiotepa. The rate of formation of diglutathionyl thiotepa was not altered, suggesting that the formation of diglutathionyl thiotepa is not catalyzed by GST A1-1. The role of purified human GST on the formation of monoglutathionyl thiotepa was further studied by HPLC. In incubations with 0.2 mM thiotepa, 1 mM GSH, and 40 microM GST, both GST A1-1 and P1-1 enhanced the formation of the monoglutathionyl conjugate 30-35-fold above the nonenzymatic formation, while GST A2-2 and M1a-1a did not catalyze the rate of formation of this conjugate. Kms for the GST A1-1 (alpha) and P1-1 (pi) catalyzed formation of monoglutathionyl thiotepa were in the 5-7 mM range. Since the pH in tumors might be lower than in normal cells, the pH dependency of the GST P1-1 catalyzed formation of monoglutathionyl thiotepa was also studied. At all pHs tested (range, 5.5-8.5), a marked catalytic effect of both GST P1-1 and A1-1 on the formation of monoglutathionyl conjugates was noted. The role of GST on the formation of monoglutathionyl conjugates of tepa (tris(1-aziridinyl)phosphine oxide), the major metabolite formed from thiotepa, was also studied. Both GST A1-1 and P1-1 could enhance the formation of the glutathione conjugate 37-46-fold above the spontaneous levels, while GST M1a-1a and A2-2 again did not increase the rate of formation of this conjugate. The results of these studies show that the aziridine moieties in thiotepa/tepa are substrates for both GST A1-1 and P1-1. Thus, GST catalyzed glutathione conjugation of thiotepa might be an important factor in the development of drug resistance towards thiotepa.

The effect of di(ethylhexyl)phthalate on fatty acid oxidation and carnitine palmitoyltransferase in various rat tissues.

Male rats were fed a diet with or without 2% di(2-ethylhexyl)phthalate (DEHP) for 12 days. Total and peroxisomal oxidation rates of palmitic and arachidonic acid were increased in homogenates of liver and kidney after DEHP administration. The relative peroxisomal contribution to the total oxidation was only higher in liver. The activities of acyl-CoA oxidase and carnitine palmitoyltransferase were also higher in both tissues. Immunoblots showed that the increase of fatty acid oxidation was associated with a higher concentration of enzymes of peroxisomal and mitochondrial beta-oxidation. DEHP did not change total and peroxisomal fatty acid oxidation and activity of carnitine palmitoyltransferase of homogenates of heart and skeletal muscle. The cause for the tissue-specific response is discussed.

Microsomal lauric acid hydroxylase activities after treatment of rats with three classical cytochrome P450 inducers and peroxisome proliferating compounds.

In order to investigate a proposed relationship between induction of hepatic microsomal lauric acid hydroxylase activity and peroxisome proliferation in the liver, male Wistar rats were treated with peroxisome proliferating compounds, and the lauric acid hydroxylase activity, the immunochemical detectable levels of cytochrome P450 4A1 and the activities of peroxisomal enzymes were determined. In addition, the levels of cytochrome P450 4A1 and lauric acid hydroxylase activities were studied after treatment of rats with three cytochrome P450 inducers. After treatment with aroclor-1254, phenobarbital or 3-methylcholanthrene total cytochrome P450 was 1.7-2.7 times induced. However, no induction of lauric acid omega-hydroxylase activities or P450 4A1 levels were found. After treatment of rats with di(2-ethylhexyl)phthalate (DEHP) a dose-dependent induction of lauric acid omega-hydroxylase activities, levels of cytochrome P450 4A1 and peroxisomal fatty acid beta-oxidation was found. Even at a dose-level of 100 mg DEPH/kg body weight per day a significant induction of these activities was observed. The main metabolites of DEHP, mono(2-ethylhexyl)phthalate and 2-ethyl-1-hexanol, also caused an induction of levels of P450 4A1, lauric acid omega-hydroxylase activities and the activity of peroxisomal palmitoyl-CoA oxidase. 2-Ethyl-1-hexanoic acid did not influence lauric acid omega-hydroxylase activities, but did induce levels of P450 4A1 and palmitoyl-CoA oxidase activities. Three other compounds (perfluoro-octanoic acid, valproate and nafenopin) induced both lauric acid omega-hydroxylase activity and peroxisomal palmitoyl-CoA oxidase activity. The plasticizer, di(2-ethylhexyl)adipate, did not induce levels of P450 4A1, lauric acid omega-hydroxylase activities or palmitoyl-CoA oxidase activities. With the compounds tested a close association between the induction of lauric acid omega-hydroxylase activities and peroxisomal palmitoyl-CoA oxidase activity was found. These data support the theory that peroxisome proliferating compounds do induce lauric acid omega-hydroxylase activities and that there might be a mechanistic inter-relationship between peroxisome proliferation and induction of lauric acid omega-hydroxylase activities.

Effects of the peroxisome proliferator mono(2-ethylhexyl)phthalate in primary hepatocyte cultures derived from rat, guinea pig, rabbit and monkey. Relationship between interspecies differences in biotransformation and peroxisome proliferating potencies.

Primary hepatocyte cultures derived from rat, rabbit, guinea pig and monkey have been treated in vitro with metabolites of di(2-ethylhexyl)phthalate, i.e. mono(2-ethylhexyl)phthalate (MEHP), mono(5-carboxy-2-ethylpentyl)phthalate (metabolite V) and mono(2-ethyl-5-oxohexyl)phthalate (metabolite VI). In rat hepatocyte cultures MEHP and metabolite VI were equally potent in inducing peroxisome proliferation, while metabolite V was much less potent. In rat hepatocytes a 50% increase in both peroxisomal palmitoyl-CoA oxidase activity and microsomal lauric acid omega-hydroxylation activity was found after treatment with 5-15 microM MEHP. In guinea pig, rabbit and monkey hepatocyte cultures, a 50% increase in peroxisomal palmitoyl-CoA oxidase activity was found after treatment with 408-485 microM MEHP. No induction of lauric acid omega-hydroxylation activity was found. These results indicate that peroxisome proliferation can be induced by MEHP in rabbit, guinea pig and monkey hepatocytes, but that these species are at least 30-fold less sensitive to peroxisome proliferation induction than rats. The proposed mechanistic inter-relationship between induction of lauric acid omega-hydroxylation activity and peroxisome proliferation is found in rat hepatocytes, but not in hepatocytes of the other three species. Treatment of guinea pig hepatocyte cultures with MEHP resulted in an increase in triglyceride concentrations in the hepatocytes. In rat and rabbit hepatocyte cultures, triglyceride concentrations were much less altered by MEHP. In monkey hepatocytes a decrease in hepatic triglyceride concentration was found after treatment with MEHP. These effects are in agreement with in vivo effects observed before. After treatment of primary hepatocyte cultures with MEHP, high concentrations of omega- and (omega-1)-hydroxylated metabolites of MEHP were found in media from rat, rabbit and guinea pig cultures. The formation of these metabolites did not decline in time. During treatment the metabolite profile in media from rat hepatocyte cultures moved towards omega-hydroxy metabolites of MEHP. In media from monkey hepatocyte cultures the lowest concentrations of hydroxylated metabolites were determined. No major species differences were found in the potency to form oxidized MEHP metabolites, and thus no unique metabolite differences were found, which could explain the species differences in sensitivity for peroxisome proliferation.

Gas supersaturation in the cecal wall of mice due to bacterial CO2 production.

PCO2 in the lumen and serosa of cecum and jejunum was measured in mice. The anesthetic used was a fentanyl-fluanisone-midazolam mixture. PCO2 was recorded in vivo and postmortem. PCO2 was 409 +/- 32 Torr (55 +/- 4 kPa) in the cecal lumen and 199 +/- 22 Torr (27 +/- 3 kPa) on the serosa in normal mice. Irrigation of the cecum resulted in serosal and luminal PCO2 levels of 65-75 Torr. Cecal PCO2 was significantly lower in germ-free mice (65 +/- 5 Torr). Cecal PCO2 increased significantly after introduction of normal bacterial flora into germ-free mice. Introduction of bacterial monocultures into germ-free mice had no effect. After the deaths of the mice, cecal PCO2 increased rapidly in normal mice. The intestinal bacteria produced the majority of the cecal PCO2, and the use of tonometry in intestinal segments with a high bacterial activity should be interpreted with caution. We propose that serosal PCO2 levels >150-190 Torr (20-25 kPa) in the cecum of mice with a normal circulation may represent a state of gas supersaturation in the cecal wall.

Effect of di(2-ethylhexyl)phthalate on enzyme activity levels in liver and serum of rats.

In order to identify non-invasive, biochemical indicators of di(2-ethylhexyl)phthalate (DEHP) exposure, we have compared the effects in blood serum with biochemical effects in liver in rats fed a diet containing 0, 0.25, 0.75 and 2% DEHP for 2 weeks. After 3 days of treatment serum arylesterase activity levels and serum triglycerides were decreased to 60% and 20% of control values, respectively. After a 2-week treatment with DEHP the effects were generally stronger. Compared to a control group, serum arylesterase activity levels, serum triglycerides and serum cholesterol were decreased to 40%, 20% and 50%, respectively. Serum cholinesterase activity levels and serum albumin concentrations were increased by the DEHP treatment to 290% and 135% of control values, respectively. In the livers a hepatomegaly, an induction of cytochrome P-450 IVA1 and induction of the activity of palmitoyl-CoA oxidase and carnitine acetyl-CoA transferase was found to be 180%, 1080%, 1300% and 1700% of control values, respectively. The liver is a more sensitive target for DEHP exposure compared to the biochemical effects in serum, but determination of the serum parameters can be used to determine early biological effects of exposure to DEHP.

The interaction of glutathione with 4-hydroxycyclophosphamide and phosphoramide mustard, studied by 31P nuclear magnetic resonance spectroscopy.

Development of resistance of cancer cells against cyclophosphamide (CP) is probably associated with an increased conjugation with glutathione. 31P NMR spectroscopy was used to monitor the time courses for the chemical conjugation with glutathione of the CP metabolites 4-hydroxycyclophosphamide (4-OHCP) and phosphoramide mustard (PM) at 24 degrees C. PM incubated with a 10-fold molar excess of glutathione showed a disappearance of the PM signal (t1/2 = 112 min), accompanied by an increase of two signals, attributed to the intermediate PM monoglutathione conjugate and the PM diglutathione conjugate. After 680 min, only a signal assigned to the PM diglutathione conjugate was found. This conjugate was relatively stable. The formation of the PM diglutathione conjugate was confirmed with fast atom bombardment mass spectrometry (FAB-MS). The rate constant for the disappearance of the PM signal in incubations with glutathione was 6.2 x 10(-3) min-1, and was 5.4 x 10(-3) min-1 in incubations without glutathione, indicating that the rate-limiting step in both reactions in the formation of aziridinium ions. When 4-OHCP was incubated with a 10-fold molar excess of glutathione, six signals was found which were not present in spectra of incubations without glutathione. In addition to the signals assigned to the mono- and diglutathionyl conjugates of PM, four signals were found of which the pattern of formation in time was identical. These four signals correspond to the four stereoisomers of 4-glutathionylcyclophosphamide (4-GSCP). The formation of 4-GSCP was confirmed with FAB-MS. Within 120 min after the start of the reaction no free 4-OHCP or aldophosphamide signals were found in the spectra. Free PM was detected in all spectra indicating that degradation of 4-GSCP gives rise to PM, the ultimate cytotoxic metabolite of CP, 4-GSCP therefore appears an important pool of phosphoramide mustard, which in turn can be deactivated by glutathione.

Non-mutagenicity of 4 metabolites of di(2-ethylhexyl)phthalate (DEHP) and 3 structurally related derivatives of di(2-ethylhexyl)adipate (DEHA) in the Salmonella mutagenicity assay.

Four metabolites of the rat liver carcinogen di(2-ethylhexyl)phthalate (DEHP) (mono-(2-ethylhexyl)phthalate, mono-(2-ethyl-5-hydroxyhexyl)phthalate, mono-(2-ethyl-5-oxohexyl)phthalate, and mono-(5-carboxy-2-ethylpentyl)phthalate) and 3 structurally related derivatives of di(2-ethylhexyl)adipate (DEHA) (mono-(2-ethylhexyl)adipate, mono-(2-ethyl-5-hydroxyhexyl)adipate, and mono-(2-ethyl-5-oxohexyl)adipate) were tested for mutagenicity in the Ames assay using Salmonella typhimurium strains TA97, TA98, TA100, and TA102, with and without a metabolic activation preparation. Aroclor 1254-induced rat liver S9 and DEHP-induced rat liver S9 were used. Concentrations of these compounds up to 1000 micrograms/plate were negative with all tester strains in the presence or absence of metabolic activation.

S-phenyl-N-acetylcysteine in urine of rats and workers after exposure to benzene.

An HPLC method for the determination of S-phenyl-N-acetylcysteine in urine is described. The sensitivity is 6 mumol/L (CV = 9%) urine. Exposure of rats to six different concentrations of benzene, ranging from 0-30 ppm, was highly associated with urinary excretion of S-phenyl-N-acetylcysteine (r = 0.86) and with total phenol (r = 0.81). A background level of phenol was found in urine of both non-exposed rats and of non-exposed referents. However, no background excretion of S-phenyl-N-acetylcysteine was found, either in rats or in humans. In urine of exposed rats, the level of S-phenyl-N-acetylcysteine was approximately five times lower than the phenol level. Workers occupationally exposed to benzene, showing high levels of urinary phenol, revealed low concentrations of urinary S-phenyl-N-acetylcysteine. The biological monitoring of industrial exposure to benzene by determination of S-phenyl-N-acetylcysteine in urine is not better than the determination of phenol in urine.

Determination of four metabolites of the plasticizer di(2-ethylhexyl)phthalate in human urine samples.

A method for biological monitoring of exposure to the plasticizer di(2-ethylhexyl)phthalate (DEHP) is described. In this method the four main metabolites of DEHP [i.e., mono(2-ethylhexyl)phthalate (MEHP), mono(5-carboxy-2-ethylpentyl)phthalate, mono(2-ethyl-5-oxohexyl)phthalate, and mono(2-ethyl-5-hydroxyhexyl)-phthalate] are determined in urine samples. The procedure includes enzymatic hydrolysis, ether extraction, and derivatization with triethyloxonium tetrafluoroborate. Analysis is performed by gas chromatography-electron impact mass spectrometry. The detection limit for all four metabolites is less than 25 micrograms/l urine. The coefficient of variation based on duplicate determinations of urine samples of workers occupationally exposed to DEHP was 16% for MEHP (mean concentration 0.157 mg/l) and 6%-9% for the other three metabolites (mean concentrations 0.130-0.175 mg/l). The method described here was used to study DEHP metabolism in man. Most persons excrete mono(2-ethyl-5-oxohexyl)-phthalate and mono(2-ethyl-5-hydroxyhexyl)phthalate as a (glucuronide) conjugate. Mono(5-carboxy-2-ethylpentyl)phthalate is mainly excreted in free form, while for MEHP a large interindividual variation in conjugation status was observed. Of the four metabolites quantified, 52% are products of a (omega-1)-hydroxylation reaction of MEHP [i.e., mono(2-ethyl-5-oxohexyl)phthalate and mono(2-ethyl-5-hydroxylation reaction of MEHP [i.e., mono(5-carboxy-2-ethylpentyl)phthalate], and 26% is not oxidized further (i.e., MEHP). A good correlation is obtained when the amount of MEHP omega-hydroxylation products is compared with the amount of MEHP (omega-1)-hydroxylation products in urine samples. When the internal dose of DEHP has to be established we recommend that the levels of all four metabolites of DEHP be studied in urine samples.

Determination of the cytochrome P-450 IV marker, omega-hydroxylauric acid, by high-performance liquid chromatography and fluorimetric detection.

The formation of omega-hydroxylauric acid from lauric acid is an indicator of the activity of cytochrome P-450 IV family proteins. The two main metabolites of lauric acid, (omega-1)-and omega-hydroxylauric acid, have been completely separated by reversed-phase high-performance liquid chromatography. Measurement of lauric acid hydroxylase activity in microsomal liver samples, based on derivatization of the substrate and metabolites with the fluorescent agent 4-bromomethyl-6,7-dimethoxycoumarin, is a precise method (coefficient of variation = 7.6 and 10% for omega and (omega-1) metabolites, respectively) with good sensitivity (signal-to-noise ratio in microsomal samples of untreated rats greater than 20). In microsomal fractions from livers of rats treated with di-(2-ethylhexyl)phthalate the extent of omega-hydroxylation of lauric acid increased dose-dependently (ca. ten-fold). The (omega-1)-hydroxylase activity was not altered. A strong correlation between immunochemically determined cytochrome P-450 IVA1 and lauric acid omega-hydroxylase activity was found (r = 0.94, n = 30).

Etiology of cecal and hepatic lesions in mice after administration of gas-carrier contrast agents used in ultrasound imaging.

The aim of the study was to investigate the etiology of cecal and hepatic lesions in mice and rats after intravenous administration of gas-carrier contrast agents (GCAs). A modified fluorescein flowmetry technique and 24 h necropsy were used in mice (conventional and germ free), rats, and guinea pigs after GCA administration. Different diets and oral nonabsorbable antibiotics were used. Nonfluorescence, edema, congestion, hemorrhage, and mucosal erosion in cecum and colon and nonfluorescent areas in the liver were observed from 16 min after GCA administration in conventional mice on standard diet. Numerous gas bubbles (>50 microm) were observed in the vasculature around the nonfluorescent areas of cecum and colon and in mesenteric vessels draining to the portal vein. Acute inflammation, edema, hemorrhage, and ulceration of the cecum and colon and liver necrosis were seen 24 h after GCA administration in conventional mice on standard diet. When mice were maintained on either a diet with glucose as the only carbohydrate source or on a standard diet supplemented with antibiotics, uniform fluorescence and no organ lesions were observed after GCA administration. Uniform fluorescence and no organ lesions were observed in germ-free mice, rats, and guinea pigs dosed with GCAs and in control animals (mice, rats, and guinea pigs) dosed with sucrose. The results indicate that intravascular growth of GCA microbubbles occurs in the cecal and colonic wall of mice, leading to occlusive ischemia and necrosis in these intestinal segments and secondary gas embolisation in the liver. Transmural gas supersaturation in the cecal wall may explain the intravascular bubble growth in mice.