Fecal metabolomics reveals products of dysregulated proteolysis and altered microbial metabolism in obesity-related osteoarthritis.

OBJECTIVE: The objective of this exploratory study was to determine if perturbations in gut microbial composition and the gut metabolome could be linked to individuals with obesity and osteoarthritis (OA). METHODS: Fecal samples were collected from obese individuals diagnosed with radiographic hand plus knee OA (n = 59), defined as involvement of at least 3 joints across both hands, and a Kellgren-Lawrence (KL) grade 2-4 (or total knee replacement) in at least one knee. Controls (n = 33) were without hand OA and with KL grade 0-1 knees. Fecal metabolomes were analyzed by a UHPLC/Q Exactive HFx mass spectrometer. Microbiome composition was determined in fecal samples by 16 S ribosomal RNA amplicon sequencing (rRNA-seq). Stepwise logistic regression models were built to determine microbiome and/or metabolic characteristics of OA. RESULTS: Untargeted metabolomics analysis indicated that OA cases had significantly higher levels of di- and tripeptides and significant perturbations in microbial metabolites including propionic acid, indoles, and other tryptophan metabolites. Pathway analysis revealed several significantly perturbed pathways associated with OA including leukotriene metabolism, amino acid metabolism and fatty acid utilization. Logistic regression models selected metabolites associated with the gut microbiota and leaky gut syndrome as significant predictors of OA status, particularly when combined with the rRNA-seq data. CONCLUSIONS: Adults with obesity and knee plus hand OA have distinct fecal metabolomes characterized by increased products of proteolysis, perturbations in leukotriene metabolism, and changes in microbial metabolites compared with controls. These metabolic perturbations indicate a possible role of dysregulated proteolysis in OA.

CYP2E1-catalyzed oxidation contributes to the sperm toxicity of 1-bromopropane in mice.

1-bromopropane (1-BrP) induces dose- and time-dependent reproductive organ toxicity and reduced sperm motility in rodents. The contribution of cytochrome P4502E1 (CYP2E1) to both 1-BrP metabolism and the induction of male reproductive toxicity was investigated using wild-type (WT) and Cyp2e1-/- mice. In gas uptake inhalation studies, the elimination half-life of [1,2,3-(13)C]-1-BrP was longer in Cyp2e1-/- mice relative to WT (3.2 vs. 1.3 h). Urinary metabolites were identified by 13C nuclear magnetic resonance. The mercapturic acid of 1-bromo-2-hydroxypropane (2OHBrP) was the major urinary metabolite in WT mice, and products of conjugation of 1-BrP with glutathione (GSH) were insignificant. The ratio of GSH conjugation to 2-hydroxylation increased 5-fold in Cyp2e1-/- mice relative to WT. After 1-BrP exposure, hepatic GSH was decreased by 76% in WT mice vs. 47% in Cyp2e1-/- mice. Despite a 170% increase in 1-BrP exposure in Cyp2e1-/- vs. WT mice, sperm motility in exposed Cyp2e1-/- mice did not change relative to unexposed matched controls. This suggests that metabolites produced through CYP2E1-mediated oxidation may be responsible for 1-BrP-induced sperm toxicity. Both 1-BrP and 2OHBrP inhibited the motility of sperm obtained from WT mice in vitro. However, only 2OHBrP reduced the motility of sperm obtained from Cyp2e1-/- mice in vitro, suggesting that conversion of parent compound to 2OHBrP within the spermatozoa may contribute, at least in part, to reduced motility. Overall, these data suggest that metabolism of 1-BrP is mediated in part by CYP2E1, and activation of 1BrP via this enzyme may contribute to the male reproductive toxicity of this chemical.

Metabolism and disposition of 1-bromopropane in rats and mice following inhalation or intravenous administration.

Workplace exposure to 1-bromopropane (1-BrP) can potentially occur during its use in spray adhesives, fats, waxes, and resins. 1-BrP may be used to replace ozone depleting solvents, resulting in an increase in its annual production in the US, which currently exceeds 1 million pounds. The potential for human exposure to 1-BrP and the reports of adverse effects associated with potential occupational exposure to high levels of 1-BrP have increased the need for the development of biomarkers of exposure and an improved understanding of 1-BrP metabolism and disposition. In this study, the factors influencing the disposition and biotransformation of 1-BrP were examined in male F344 rats and B6C3F1 mice following inhalation exposure (800 ppm) or intravenous administration (5, 20, and 100 mg/kg). [1,2,3-(13)C]1-BrP and [1-(14)C]1-BrP were administered to enable characterization of urinary metabolites using NMR spectroscopy, LC-MS/MS, and HPLC coupled radiochromatography. Exhaled breath volatile organic chemicals (VOC), exhaled CO(2), urine, feces, and tissues were collected for up to 48 h post-administration for determination of radioactivity distribution. Rats and mice exhaled a majority of the administered dose as either VOC (40-72%) or (14)CO(2) (10-30%). For rats, but not mice, the percentage of the dose exhaled as VOC increased between the mid ( approximately 50%) and high ( approximately 71%) dose groups; while the percentage of the dose exhaled as (14)CO(2) decreased (19 to 10%). The molar ratio of exhaled (14)CO(2) to total released bromide, which decreased as dose increased, demonstrated that the proportion of 1-BrP metabolized via oxidation relative to pathways dependent on glutathione conjugation is inversely proportional to dose in the rat. [(14)C]1-BrP equivalents were recovered in urine (13-17%, rats; 14-23% mice), feces (<2%), or retained in the tissues and carcass (<6%) of rats and mice administered i.v. 5 to 100 mg/kg [(14)C]1-BrP. Metabolites characterized in urine of rats and mice include N-acetyl-S-propylcysteine, N-acetyl-3-(propylsulfinyl)alanine, N-acetyl-S-(2-hydroxypropyl)cysteine, 1-bromo-2-hydroxypropane-O-glucuronide, N-acetyl-S-(2-oxopropyl)cysteine, and N-acetyl-3-[(2-oxopropyl)sulfinyl]alanine. These metabolites may be formed following oxidation of 1-bromopropane to 1-bromo-2-propanol and bromoacetone and following subsequent glutathione conjugation with either of these compounds. Rats pretreated with 1-aminobenzotriazole (ABT), a potent inhibitor of P450 excreted less in urine (down 30%), exhaled as (14)CO2 (down 80%), or retained in liver (down 90%), with a concomitant increase in radioactivity expired as VOC (up 52%). Following ABT pretreatment, rat urinary metabolites were reduced in number from 10 to 1, N-acetyl-S-propylcysteine, which accounted for >90% of the total urinary radioactivity in ABT pretreated rats. Together, these data demonstrate a role for cytochrome P450 and glutathione in the dose-dependent metabolism and disposition of 1-BrP in the rat.

Disposition of [Ring-U-(14)C]styrene in rats and mice exposed by recirculating nose-only inhalation.

The disposition of styrene was studied in a group of 12 Sprague Dawley rats and two groups of 30 CD1 mice exposed separately to 160 ppm [ring-U-(14)C]styrene of high specific radioactivity of 1.92 TBq x mol(-1) (52 Ci x mol(-1)) for 6 h. A nose-only exposure system was successfully adapted to (1) recirculate a portion of the flow to limit the amount of (14)C-styrene required, and (2) avoid any polymerization of the compound. The mean uptake of styrene in rats was 113 +/- 7 micromol x kg(-1) x h(-1) and stable over time. The mean uptake in mice was higher, 189 +/- 53 and 183 +/- 76 micromol x kg(-1) x h(-1), for the first and second mouse inhalation experiment, but decreased steadily over time. Some of the mice, but none of the rats, showed signs of overt toxicity. The overall excretion of styrene and its metabolites was quantitatively similar in rats and mice. Urinary excretion was the primary route of excretion while fecal excretion accounted for only a very small part of the radioactivity. There was, however, a significant difference between mice and rats in the exhalation of (14)CO(2), which must have resulted from opening and subsequent breakdown of the aromatic ring. In mice the exhalation of (14)CO(2) accounted for 6.4 +/- 1.0 and 8. 0 +/- 0.5% of the styrene retained during the first and second mouse inhalation experiment. In rats, exhalation of (14)CO(2) accounted for only 2.0 +/- 0.7% of the retained styrene. Together with the results from the quantitative whole-body autoradiography (showing significantly higher binding in mouse lung and nasal passages compared to rat) the larger production of (14)CO(2) might be indicative of the formation of reactive ring-opened metabolites in the mouse lung, which, in turn, might be related to the observed development of bronchioalveolar tumors and nasal effects in mice exposed to styrene.

Metabolism and disposition of bisphenol A in female rats.

Bisphenol A (BPA), which is used in the manufacture of polycarbonates, elicits weak estrogenic activity in in vitro and in vivo test systems. The objectives of this study were to compare the patterns of disposition of radioactivity in adult female F-344 and CD rats after oral administration of (14)C BPA (100 mg/kg), to isolate the glucuronide of BPA and to assess its estrogenic activity in vitro, and to evaluate the transfer of radioactivity to pups from lactating dams administered (14)C BPA. Over 6 days, F-344 rats excreted more radioactivity in urine than CD rats. The major metabolite in urine was identified as bisphenol A glucuronide (BPA gluc) by incubation with beta-glucuronidase and (1)H and (13)C NMR spectroscopy. In lactating CD rats administered (14)C BPA (100 mg/kg) by gavage, only a small fraction of the label was found in milk, with 0.95 +/- 0.66, 0.63 +/- 0.13, and 0.26 +/- 0.10 microg equiv/ml (mean +/- SD) from dams collected 1, 8, and 26 h after dosing, respectively. Radioactivity in pup carcasses indicated exposure in the range of microgram equivalents per kilogram; those values ranged from 44.3 +/- 24.4 for pups separated from their lactating dams at 2 h to 78.4 +/- 10.9 at 24 h. BPA gluc was the prominent metabolite in milk and plasma. In test systems for activation of in vitro estrogen receptors alpha and beta, BPA gluc did not show appreciable efficacy at concentrations up to 0.03 mM, indicating that metabolism via glucuronidation is a detoxication reaction.

Quantification of DNA adducts formed in liver, lungs, and isolated lung cells of rats and mice exposed to (14)C-styrene by nose-only inhalation.

Bronchiolo-alveolar tumors were observed in mice exposed chronically to 160 ppm styrene, whereas no tumors were seen in rats up to concentrations of 1000 ppm. Clara cells, which are predominant in the bronchiolo-alveolar region in mouse lungs but less numerous in rat and human lung, contain various cytochrome P450s, which may oxidize styrene to the rodent carcinogen styrene-7,8-oxide (SO) and other reactive metabolites. Reactive metabolites may form specific DNA adducts and induce the tumors observed in mice. To determine DNA adducts in specific tissues and cell types, rats and mice were exposed to 160 ppm [ring-U-(14)C]styrene by nose-only inhalation for 6 h in a recirculating exposure system. Liver and lungs were isolated 0 and 42 h after exposure. Fractions enriched in Type II cells and Clara cells were isolated from rat and mouse lung, respectively. DNA adduct profiles differed quantitatively and qualitatively in liver, total lung, and enriched lung cell fractions. At 0 and 42 h after exposure, the two isomeric N:7-guanine adducts of SO (measured together, HPEG) were present in liver at 3.0 +/- 0.2 and 1.9 +/- 0.3 (rat) and 1.2 +/- 0.2 and 3.2 +/- 0.5 (mouse) per 10(8) bases. Several other, unidentified adducts were present at two to three times higher concentrations in mouse, but not in rat liver. In both rat and mouse lung, HPEG was the major adduct at approximately 1 per 10(8) bases at 0 h, and these levels halved at 42 h. In both rat Type II and non-Type II cells, HPEG was the major adduct and was about three times higher in Type II cells than in total lung. For mice, DNA adduct levels in Clara cells and non-Clara cells were similar to total lung. The hepatic covalent binding index (CBI) at 0 and 42 h was 0.19 +/- 0.06 and 0.14 +/- 0.03 (rat) and 0. 25 +/- 0.11 and 0.44 +/- 0.23 (mouse), respectively. The pulmonary CBIs, based on tissues combined for 0 and 42 h, were 0.17 +/- 0.04 (rat) and 0.24 +/- 0.04 (mouse). Compared with CBIs for other genotoxicants, these values indicate that styrene has only very weak adduct-forming potency. The overall results of this study indicate that DNA adduct formation does not play an important role in styrene tumorigenicity in chronically exposed mice.

Styrene oxide in blood, hemoglobin adducts, and urinary metabolites in human volunteers exposed to (13)C(8)-styrene vapors.

Styrene is used in the manufacture of plastics and polymers and in the boat-building industry. The major metabolic route for styrene in rats, mice, and humans involves conversion to styrene-7,8-oxide (SO). The purpose of this study was to evaluate blood SO, SO-hemoglobin (SO-Hb) adducts, and urinary metabolites in styrene-exposed human volunteers and to compare these results with data previously obtained for rodents. Four healthy male volunteers were exposed for 2 h during light physical exercise to 50 ppm (13)C(8)-styrene vapor via a face mask. Levels and time profiles of styrene in exhaled air, blood, and urine (analyzed by GC) and urinary excretion patterns of mandelic acid and phenylglyoxylic acid in urine (analyzed by HPLC) were comparable to previously published volunteer studies. Maximum levels of SO in blood (measured by GC-MS) of 2.5-12.2 (average 6.7) nM were seen after 2 h, i.e., in the first sample collected after exposure had ended. The styrene blood level in humans was about 1.5 to 2 times higher than in rats and 4 times higher than in mice for equivalent styrene exposures. In contrast the SO levels in human blood was approximately fourfold lower than in mice. The level of hydroxyphenethylvaline (determined by GC-MS-MS) in pooled blood collected after exposure was estimated as 0.3 pmol/g globin corresponding to a SO-Hb adduct increment of about 0.003 pmol/g and ppmh. NMR analyses of urine showed that a major portion (> 95%) of the excreted (13)C-derived metabolites was derived from hydrolysis of SO, while only a small percentage of the excreted metabolites (< 5%) was derived from metabolism via phenylacetaldehyde. Signals consistent with metabolites derived from other pathways of styrene metabolism in rodents (such as glutathione conjugation with SO or ring epoxidation) were not detected.

Role of cytochrome P450 2E1 in the metabolism of acrylamide and acrylonitrile in mice.

Acrylonitrile (AN) and acrylamide (AM) are commonly used in the synthesis of plastics and polymers. In rodents, AM and AN are metabolized to the epoxides glycidamide and cyanoethylene oxide, respectively. The aim of this study was to determine the role of cytochrome P450 in the metabolism of AM and AN in vivo. Wild-type (WT) mice, WT mice pretreated with aminobenzotriazole (ABT, 50 mg/kg ip, 2 h pre-exposure), and mice devoid of cytochrome P450 2E1 (P450 2E1-null) were treated with 50 mg/kg [(13)C]AM po. WT mice and P450 2E1-null mice were treated with 2.5 or 10 mg/kg [(13)C]AN po. Urine was collected for 24 h, and metabolites were characterized using (13)C NMR. WT mice excreted metabolites derived from the epoxides and from direct GSH conjugation with AM or AN. Only metabolites derived from direct GSH conjugation with AM or AN were observed in the urine from ABT-pretreated WT mice and P450 2E1-null mice. On the basis of evaluation of urinary metabolites at these doses, these data suggest that P450 2E1 is possibly the only cytochrome P450 enzyme involved in the metabolism of AM and AN in mice, that inhibiting total P450 activity does not result in new pathways of non-P450 metabolism of AM, and that mice devoid of P450 2E1 do not excrete metabolites of AM or AN that would be produced by oxidation by other cytochrome P450s. P450 2E1-null mice may be an appropriate model for the investigation of the role of oxidative metabolism in the toxicity or carcinogenicity of these compounds.

13C(2)-Labeled methyl tert-butyl ether: toxicokinetics and characterization of urinary metabolites in humans.

After exposure to methyl tert-butyl ether (MTBE), a gasoline additive, only one metabolite [tert-butyl alcohol (TBA), <1% of dose] has been identified in human urine [Nihlén, A., et al. (1998) Toxicol. Appl. Pharmacol. 148, 274-280]. In the study presented here, metabolites of MTBE were characterized by (1)H-decoupled (13)C NMR spectroscopy in urine obtained from four volunteers experimentally exposed to 50 ppm (13)C-labeled MTBE ([1,2-(13)C(2)]MTBE) vapor (facemask) for 2 h during a light physical work load (50 W). Chemical shifts for the two adjacent (13)C-labeled carbons in [1, 2-(13)C(2)]MTBE-derived metabolites were consistent with the shifts obtained for spiked standards of alpha-hydroxyisobutyric acid (HBA) and 2-methyl-1,2-propanediol (MPD). NMR signals were not detected for labeled MTBE, TBA, or possible MTBE-derived conjugates. Quantification of HBA and MPD was performed by NMR for two urine samples (collected 20 h after exposure). One subject had 11% HBA and 1% MPD, and the other individual had 3% HBA and 1% MPD in the urine, expressed as a percentage of MTBE uptake. This indicates that HBA and MPD occur at significantly higher levels in the urine (detected by NMR) than MTBE and TBA (detected by GC). To our knowledge, this is the first characterization of MTBE metabolites, other than TBA, in humans. Further urine, blood, and expired air were collected up to 22 h after exposure, and the toxicokinetics of MTBE, TBA, and acetone were determined by GC. Low relative uptake (39%), a low level of postexposure exhalation of MTBE (17%), and low recovery of TBA in the urine (<1%) were observed. The same subjects had previously been exposed to unlabeled MTBE in a whole-body exposure study [Nihlén, A., et al. (1998) Toxicol. Appl. Pharmacol. 148, 274-280], and the toxicokinetics of MTBE and TBA in this facemask exposure did not differ from the previous whole-body chamber exposure.

A physiological model for tert-amyl methyl ether and tert-amyl alcohol: hypothesis testing of model structures.

The oxygenate tert-amyl methyl ether (TAME) is a gasoline fuel additive used to reduce carbon monoxide in automobile emissions. To evaluate the relative health risk of TAME as a gasoline additive, information is needed on its pharmacokinetics and toxicity. The objective of this study was to use a physiologically-based pharmacokinetic (PBPK) model to describe the disposition of TAME and its major metabolite, tert-amyl alcohol (TAA), in male Fischer-344 rats. The model compartments for TAME and TAA were flow-limited. The TAME physiological model had 6 compartments: lung, liver, rapidly perfused tissues, slowly perfused tissues, fat, and kidney. The TAA model had 3 compartments: lung, liver, and total-body water. The 2 models were linked through metabolism of TAME to TAA in the liver. Model simulations were compared with data on blood concentrations of TAME and TAA taken from male Fischer-344 rats during and after a 6-hour inhalation exposure to 2500, 500, or 100 ppm TAME. The PBPK model predicted TAME pharmacokinetics when 2 saturable pathways for TAME oxidation were included. The TAA model, which included pathways for oxidation and glucuronide conjugation of TAA, underpredicted the experimental data collected at later times postexposure. To account for biological processes occurring during this time, three hypotheses were developed: nonspecific binding of TAA, diffusion-limited transport of TAA, and enterohepatic circulation of TAA glucuronide. These hypotheses were tested using three different model structures. Visual inspection and statistical evaluation involving maximum likelihood techniques indicated that the model incorporating nonspecific binding of TAA provided the best fit to the data. A correct model structure, based upon experimental data, statistical analyses, and biological interpretation, will allow a more accurate extrapolation to humans and, consequently, a greater understanding of human risk from exposure to TAME.

Evaluation of the metabolism and hepatotoxicity of styrene in F344 rats, B6C3F1 mice, and CD-1 mice following single and repeated inhalation exposures.

Styrene is used for the manufacture of plastics and polymers. The metabolism and hepatotoxicity (mice only) of styrene was compared in male B6C3F1 mice, CD-1 mice, and F344 rats to evaluate biochemical mechanisms of toxicity. Rats and mice were exposed to 250 ppm styrene for 6 h/day for 1 to 5 days, and liver (mice only) and blood were collected following each day of exposure. Mortality and increased serum alanine aminotransferase (ALT) activity were observed in mice but not in rats. Hepatotoxicity in B6C3F1 mice was characterized by severe centrilobular congestion after one exposure followed by acute centrilobular necrosis. Hepatotoxicity was delayed by 1 day in CD-1 mice, and the increase in ALT and degree of necrosis was less than observed for B6C3F1 mice. Following exposure to unlabeled styrene for 0, 2, or 4 days, rats and mice were exposed to [7-14C]-styrene (60 microCi/mmol) for 6 h. Urine, feces, and expired air were collected for up to 48 h. Most styrene-derived radioactivity was excreted in urine. The time-course of urinary excretion indicates that rats and CD-1 mice eliminated radioactivity at a faster rate than B6C3F1 mice following a single 250 ppm exposure, consistent with a greater extent of liver injury for B6C3F1 mice. The elimination rate following 3 or 5 days of exposure was similar for rats and both mouse strains. Following three exposures, the total radioactivity eliminated in excreta was elevated over that measured for one exposure for both mouse strains. An increased excretion of metabolites on multiple exposure is consistent with the absence of ongoing acute necrosis following 4 to 5 daily exposures. These data indicate that an induction in styrene metabolism occurs after multiple exposures, resulting in an increased uptake and/or clearance for styrene.

Urinary metabolites from F344 rats and B6C3F1 mice coadministered acrylamide and acrylonitrile for 1 or 5 days.

The purpose of this study was to examine the feasibility of using 13C NMR spectroscopy to analyze urinary metabolites produced following coadministration of two structurally similar carbon-13-labeled compounds to rodents. Acrylonitrile (AN) and acrylamide (AM) are used in the chemical industry to manufacture plastics and polymers. These compounds are known to produce carcinogenic, reproductive, or neurotoxic effects in laboratory animals. The potential for human exposure to AN and AM occurs in manufacturing facilities and environmentally. Male F344 rats and B6C3F1 mice were coadministered po [1,2,3-13C]AN (16-17 mg/kg) and [1,2,3-13C]AM (21-22 mg/kg) after 0 or 4 days of administration of unlabeled AN or AM. Urine was collected for 24 h following administration of the 13C-labeled compounds and analyzed by 13C NMR spectroscopy. Rats and mice excreted metabolites derived from glutathione (GSH) conjugation with AM or AN or derived from GSH conjugation with the epoxides cyanoethylene oxide (CEO) or glycidamide (GA). GA and its hydrolysis product were also detected in the urine of rats and mice. For mice, an increased urinary excretion of total AN- and total AM-derived metabolites (p < 0.05) on repeated coadministration suggested a possible increase in metabolism via oxidation. In addition, mice had an increased (p < 0.05) percentage of dose excreted as metabolites derived from GSH conjugation with AM, AN, CEO, or GA after five exposures as compared with one exposure that may be related to a significant increase in the synthesis of GSH or an increase in glutathione transferase activity. The only significant (p < 0.05) increase between one and five exposures for the rat was in the percentage of metabolites produced following conversion of AM to GA. The use of 13C NMR spectroscopy has provided a powerful methodology for elucidation of the metabolism of two 13C-labeled chemicals administered simultaneously.

Hepatic and pulmonary glutathione conjugation of 1,2:3,4-diepoxybutane in human, rat, and mouse in vitro.

1,3-Butadiene (BD) is a carcinogen in rats and mice. Previous in vitro studies showed that mouse liver microsomes formed 1,2-epoxy-3-butene (BMO) from BD and 1,2:3,4-diepoxybutane (BDE) from BMO at much higher rates than rat or human microsomes. Blood and tissue levels of BDE were significantly lower in rats than in mice following exposure to BD. Since mice are much more susceptible to cancer induced by BD than rats, these findings suggest a key role for BDE in BD-induced carcinogenicity. The aim of this study was to characterize the glutathione (GSH) conjugation of BDE by cytosol from human liver and mouse and rat liver and lung in vitro. BDE and radiolabeled GSH were incubated with cytosol. Conjugates were identified by 13C-NMR and FAB mass spectroscopy and quantitated by HPLC. The enzyme kinetics for the conjugation of BDE with GSH suggest that the higher BDE blood concentrations in mice compared with rats following inhalation exposure to BD are not due to differences in GSH conjugation of BDE.

Characterization of urinary metabolites from Sprague-Dawley rats and B6C3F1 mice exposed to [1,2,3,4-13C]butadiene.

1,3-Butadiene (BD) is used in the production of synthetic rubber and other resins. Carcinogenic effects have been observed in laboratory animals exposed to BD, with mice being more sensitive than rats. Metabolic oxidation of butadiene to epoxides is believed to be a crucial step in the initiation of tumors by BD. However, limited information is available that describes the in vivo metabolism of BD. Male Sprague-Dawley rats and B6C3F1 mice were exposed to 800 ppm [1,2 3,4-13C]butadiene for 5 h, and urine was collected during and for 20 h following exposure. Urinary metabolites were characterized using 1- and 2-dimensional methods of NMR spectroscopy. Three metabolites previously detected in vivo, N-acetyl-S-(2-hydroxy-3-butenyl)-L-cysteine, N-acetyl-S-(1-(hydroxymethyl)-2-propenyl)-L-cysteine, and N-acetyl-S-(3,4-dihydroxybutyl)-L-cysteine, were present in both rat and mouse urine, accounting for 87% and 73% of the total metabolites excreted, respectively. A fourth metabolite, previously detected in vitro, 3-butene-1,2-diol, was also present in both rat and mouse urine and comprised 5% and 3% of the total metabolites excreted, respectively. An additional metabolite detected only in mouse urine that is derived from glutathione conjugation with epoxybutene was identified as S-(1-(hydroxymethyl)-2-propenyl)-L-cysteine (4%). N-Acetyl-S-(1-hydroxy-3-butenyl)-L-cysteine (4%), detected in mouse urine, is a thiohemiacetal product of 3-butenal. Additionally, mice excreted N-acetyl-S-(3-hydroxypropyl)-L-cysteine (5%) and N-acetyl-S-(2-carboxyethyl)-L-cysteine (5%), which could be derived from further metabolism of N-acetyl-S-(3,4-dihydroxybutyl)-L-cysteine or from glutathione conjugation with acrolein. Mice excreted N-acetyl-S-(1-(hydroxymethyl)-3,4-dihydroxypropyl)-L-cysteine (5%), which could be derived from glutathione conjugation with diepoxybutane (BDE), while rats excreted 1,3-dihydroxypropanone (5%), which may be derived from hydrolysis of BDE. These studies indicate that reactive aldehydes are produced as metabolites of BD in vivo, in addition to the reactive monoepoxide and diepoxide of BD. The greater toxicity of BD in mice compared with rats may be attributed to the greater ability of rats to detoxify BDE via hydrolysis, and/or to the production of reactive aldehydes.

Glutathione conjugation of 1,2:3,4- diepoxybutane in human liver and rat and mouse liver and lung in vitro.

1,3-Butadiene (BD) has been classified as a probable human carcinogen based on sufficient evidence of a carcinogenic response in B6C3F1 mice and Sprague-Dawley rats and limited human evidence of carcinogenicity. Mice are much more susceptible to BD-induced carcinogenicity than rats. Previous in vitro studies revealed that mouse liver microsomes formed 1,2-epoxy-3-butene (BMO) from BD and 1,2:3,4-diepoxybutane (BDE) from BMO at much higher rates than rat or human microsomes. BDE was also readily quantitated in blood and tissues of mice exposed to BD but could not be detected in rats similarly exposed. These findings suggest a key role for BDE in BD-induced carcinogenicity. The purpose of this study was to characterize the glutathione (GSH) conjugation of BDE by liver and lung cytosol from B6C3F1 mice and Sprague-Dawley rats and human liver cytosol from six different individuals in vitro. BDE and glycine-[2-3H]GSH were incubated, at pH 7.4, with cytosol. 13C NMR and mass spectral analysis indicated formation of two isomeric conjugates, S-(1-(hydroxy-methyl)-2,3-epoxypropyl)glutathione and S-(2-hydroxy-3,4-epoxy--butyl)glutathione, which were rapidly hydrolyzed in cytosol to the corresponding trihydroxy conjugates. Total conjugates were quantitated by HPLC. Conjugation of BDE with GSH followed Michaelis-Menten kinetics in human as well as rat and mouse cytosolic fractions. The conjugation rates in mouse and rat liver cytosol were similar (Vmax 162 +/- 16 and 186 +/- 37 nmol/mg protein/min, respectively) and an order of magnitude higher than in human liver cytosol (Vmax 6.4 +/- 1.9 nmol/mg protein/min). the apparent KM values were lower in human (2.1 +/- 1.4 mM) than mouse (6.4 +/- 1.6 mM) or rat (24 +/- 6 mM) liver. Mouse lung cytosol (Vmax 38.5 +/- 2.5 nmol/mg protein/min, KM 1.70 +/- 0.37mM) is also more efficient in GSH conjugation than rat lung cytosol (Vmax 17.1 +/- 3.0 nmol/mg protein/min, KM +/- 1.7 mM). These results suggest that the higher BDE blood concentrations in mice compared with rats following inhalation exposure to BD are not due to differences in hepatic or pulmonary GSH conjugation of BDE. Also, considering the low oxidation rates of BD to BMO and of BMO to BDE in humans as compared to mice, the relatively low capacity of GSH conjugation of BDE in human liver will not necessarily lead to increased BDE blood levels in humans potentially exposed to BD.

Characterization of phosphodiester adducts produced by the reaction of cyanoethylene oxide with nucleotides.

Cyanoethylene oxide (CEO), a putative toxic and carcinogenic metabolite of acrylonitrile, is a direct-acting mutagen. The focus of this study was to elucidate potential adducts responsible for the mutagenic effect of CEO by characterizing products from the reaction of CEO with nucleotides. The reaction of CEO with the 5'-monophosphates of deoxyguanosine, deoxyadenosine, deoxycytidine or deoxythymidine resulted in the formation of at least one adduct for each nucleotide. Using two-dimensional NMR spectroscopy and fast atom bombardment mass spectrometry, CEO-nucleotide adducts (approximately 25% modification) were characterized as 2-cyano-2-hydroxyethyl phosphodiesters. The isolate from the reaction of deoxyguanosine-5'-monophosphate (dGMP) with CEO contained a second adduct, identified as N7-(2-cyano-2-hydroxyethyl)-dGMP. Single and double strand breaks, which were observed in supercoiled pBR322 plasmid DNA exposed to CEO (> 50 mM), may arise following formation of cyanohydroxyethyl phosphotriester adducts. The characterization of these phosphodiester adducts in vitro may provide insight into the intermediates responsible for the genotoxic effect of CEO in vivo.

Dose-dependent urinary excretion of acrylonitrile metabolites by rats and mice.

The dose dependence of the urinary excretion of acrylonitrile (ACN) metabolites was studied after oral administration of [2,3-14C]ACN to male F-344 rats (0.09 to 28.8 mg/kg) and male B6C3F1 mice (0.09 to 10.0 mg/kg). Urine was the major route of excretion of ACN metabolites (77 to 104% of the dose), with less than 8% of the dose excreted in the feces. Reverse-phase HPLC analysis of urine from treated animals indicated five major components (1 through 5 in order of elution) that accounted for 75 to 100% of the total urinary radioactivity. Component 4 was observed in the urine of ACN-treated mice but was only present in trace amounts in the urine of ACN-treated rats. Components 1, 2, and 3 were present in the urine of animals administered [2,3-14C]cyanoethylene oxide (CEO), indicating that these components were derived from the epoxide metabolite of ACN. The ACN urinary metabolites were isolated by HPLC and identified by chromatographic and mass spectral analysis. Component 5 was N-acetyl-S-(2-cyanoethyl)cysteine and component 4 was S-(2-cyanoethyl)thioacetic acid, both derived from the glutathione (GSH) conjugate of ACN. Component 3 contained N-acetyl-S-(2-hydroxyethyl)cysteine, N-acetyl-S-(carboxymethyl)cysteine, and N-acetyl-S-(1-cyano-2-hydroxyethyl)cysteine. Component 2 was thiodiglycolic acid. These urinary metabolites are derived from catabolism of the GSH conjugates of CEO. The polar component 1 was not identified. These results demonstrate that GSH conjugation is the major disposition pathway of ACN. The excretion of metabolites derived from CEO was an approximately linear function of dose in both species, whereas the excretion of N-acetyl-S-(2-cyanoethyl)cysteine increased nonlinearly with dose. This nonlinearity indicates the presence of a saturable pathway competing with glutathione for ACN, most likely the cytochrome P450-dependent oxidation of ACN. Thiodiglycolic acid was formed 10-fold more in mice than in rats, but this species difference in the oxidative processing of GSH conjugates is probably not of toxicological significance. The ratio of ACN epoxidation to GSH conjugation was 0.50 in rats and 0.67 in mice. This species difference in ACN oxidation could have important toxicological implications, since CEO is believed to mediate the carcinogenic effects of ACN.

A possible mechanism for the formation of 14CO2 via 2-methoxyacetic acid in mice exposed to 14C-labeled 2-methoxyethanol.

Small amounts (6-12%) of radioactivity administered by gavage as 14C-labeled 2-methoxyethanol (2-ME) or 2-methoxyacetic acid (2-MAA) to pregnant mice are exhaled as 14CO2 as well as accumulated in tissues that are highly active in the synthesis of macromolecules (Sleet et al., Toxicol. Appl. Pharmacol. 84, 25-35, 1986; Mebus et al., Toxicol. Appl. Pharmacol. 112, 87-94, 1992). In addition, pregnant CD-1 mice similarly administered 13C-labeled 2-ME excrete urinary metabolites that may arise from incorporation of a coenzyme A thioester of 2-MAA into the Krebs cycle, forming methoxycitrate (Sumner et al., Chem. Res. Toxicol. 5, 553-560, 1992). Based on these previously published observations, we propose a mechanism for the further metabolism of methoxycitrate that is consistent with the detection of 14CO2 after administering either [1-14C]2-MAA, [2-14C]2-ME, or [methoxy-14C]2-ME to mice. This postulated pathway may also explain the tissue-specific accumulation of radioactivity arising from [14C]2-ME.

Conformational analysis of receptor selective tachykinin analogs: senktide and septide.

The conformational behavior in solution of two receptor selective tachykinin agonists, senktide (succinyl-D-F-MeF-G-L-M-NH2) and septide (pQ-F-F-P-L-M-NH2) is described. Two dimensional cross relaxation NMR spectroscopy is used together with coupling constant data to obtain interproton distance constraints. These results are used in conjunction with semi-empirical energy computations to indicate favorable conformations. Senktide is found to have a high degree of conformational order which is attributed to rotational restriction associated with the N-methylation of phenylalanine. The lowest energy conformation in accord with the experimental interproton distances contains a beta-turn. Interproton distances indicate that septide exists as a random coil or in an extended chain conformation. Energy computations suggest that septide is primarily an extended chain with internal reorientation restricted by the proline residue. These results may be related to the selectivity of these peptides for different receptors, in that the analogs, with conformations more stable than tachykinins, are more receptor selective.