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The Toxicologist - Society of Toxicology

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1820 RAT LIVER MICROSOMES ENANTIOSELECTIVELY<br />

CATALYZE THE FORMATION OF HYDROXYLATED<br />

METABOLITES OF 2, 2’, 3, 3’, 6, 6’-<br />

HEXACHLOROBIPHENYL (PCB136).<br />

I. Kania-Korwel 1 , M. W. Duffel 2 , S. Bandiera 3 and H. Lehmler 1 . 1 Department <strong>of</strong><br />

Occupational and Environmental Health, University <strong>of</strong> Iowa, Iowa City, IA,<br />

2 Division <strong>of</strong> Medicinal and Natural Products Chemistry, University <strong>of</strong> Iowa, Iowa<br />

City, IA and 3 Faculty <strong>of</strong> Pharmaceutical Sciences, University <strong>of</strong> British Columbia,<br />

Vancouver, BC, Canada.<br />

Chiral PCB congeners such as PCB136 undergo enantiomeric enrichment in vivo.<br />

<strong>The</strong> biotransformation processes responsible for this enantiomeric enrichment are<br />

still poorly understood. A series <strong>of</strong> metabolism studies was performed to test the hypothesis<br />

that metabolism <strong>of</strong> PCB136 is enantioselective and is<strong>of</strong>orm-dependent in<br />

liver microsomes from rats treated with phenobarbital (PB, CYP2B induced), dexamethasone<br />

(DEX, CYP3A induced) or corn oil (CO). Incubations <strong>of</strong> all three<br />

types <strong>of</strong> microsomes with racemic PCB136 (50 μM) resulted in the time-dependent<br />

formation <strong>of</strong> hydroxylated metabolites. Microsomes from PB-treated animals<br />

generated the highest amount <strong>of</strong> metabolites, followed by microsomes from DEX<br />

and CO- treated rats. <strong>The</strong> major metabolite in all preparations was 5-OH-PCB 136<br />

and the rank order was 5-OH-PCB 136 > 4-OH-PCB136 > 4,5-diOH-PCB136.<br />

However, the relative contribution <strong>of</strong> 4-OH-PCB136 depended on the microsomal<br />

preparation and increased in microsomes from DEX and CO-treated rats. Carbon<br />

monoxide inhibited the formation <strong>of</strong> metabolites, which is consistent with the involvement<br />

<strong>of</strong> cytochrome P450 is<strong>of</strong>orms in the metabolism <strong>of</strong> PCB136.<br />

Incubation <strong>of</strong> microsomal preparations from both PB- and DEX-treated rats with<br />

(+)-, (-)-, and racemic PCB 136 revealed no clear differences in metabolite pr<strong>of</strong>iles.<br />

Although no enantiomeric enrichment <strong>of</strong> PCB136 was observed, the second eluting<br />

atropisomers <strong>of</strong> 4-OH-PCB136 and 5-OH-PCB136 were slightly enriched in<br />

incubations with racemic PCB136. Incubations with pure PCB 136 atropisomers<br />

demonstrated that the second eluting atropisomers <strong>of</strong> both metabolites are formed<br />

from (+)-PCB136. Overall, these studies demonstrate the enantioselective and is<strong>of</strong>orm-dependent<br />

formation <strong>of</strong> hydroxylated PCB 136 metabolites by cytochrome<br />

P450 enzymes (Supported by NIH ES017425).<br />

1821 MYELOPEROXIDASE-MEDIATED BIOACTIVATION OF<br />

5-HYDROXYTHIABENDAZOLE: A POSSIBLE<br />

MECHANISM BEHIND THE TOXICITIES ASSOCIATED<br />

WITH THIABENDAZOLE.<br />

J. Jamieson, E. Smith, D. Dalvie, G. Stevens and G. Yanochko. Pfizer, Inc., San<br />

Diego, CA.<br />

Thiabendazole (TBZ), an antihelminthic and antifungal agent, is associated with a<br />

host <strong>of</strong> adverse effects including nephrotoxicity, hepatotoxicity, and teratogenicity.<br />

Bioactivation <strong>of</strong> the primary metabolite <strong>of</strong> TBZ, 5-hydroxythiabendazole, has been<br />

proposed to yield a reactive intermediate. Here we show that this reactive intermediate<br />

can be generated by myeloperoxidase, a neutrophil-bourne peroxidase. Using<br />

a cell viability endpoint, we examined the toxicity <strong>of</strong> TBZ, 5OH-TBZ, and MPOgenerated<br />

metabolites in cell-based models including primary rat proximal tubule<br />

epithelial cells, NRK-52E rat proximal tubule cells, and H9C2 rat myocardial cells.<br />

Timecourse experiments with MPO showed complete turnover <strong>of</strong> 5OH-TBZ<br />

within 15 minutes and a dramatic leftward shift in dose-response curves after 12<br />

hours. After a 24 hour exposure in vitro, the LC50 <strong>of</strong> this reactive intermediate was<br />

22 ± 1μM compared to 117 ± 20μM from 5OH-TBZ alone, a greater than 5-fold<br />

decrease. LC50 values were equal in all cell types used. This toxicity can be completely<br />

rescued via incubation with rutin, an inhibitor <strong>of</strong> MPO. <strong>The</strong>se results suggest<br />

that MPO-mediated biotransformation <strong>of</strong> 5OH-TBZ yields a reactive intermediate<br />

which may play a role in TBZ-induced toxicity.<br />

1822 METABOLISM OF 2-HYDROXY-4-<br />

METHOXYBENZOPHENONE DEPENDS ON SPECIES<br />

AND SEX.<br />

C. Wegerski 1 , S. S. Auerbach 2 , J. M. Sanders 2 , M. Doyle-Eisele 1 and J. D.<br />

McDonald 1 . 1 Lovelace Respiratory Research Institute, Albuquerque, NM and<br />

2 NTP/NIEHS, Research Triangle Park, NC.<br />

Metabolism and disposition studies <strong>of</strong> 2-Hydroxy-4-methoxybenzophenone<br />

(HMB) are being conducted to aid in interpretation <strong>of</strong> toxicology results and interspecies<br />

and sex extrapolation. To assess species and sex differences within rodents, in<br />

vivo studies were conducted by oral dose administration <strong>of</strong> 14C labeled HMB in<br />

male and female Sprague-Dawley rats and B6C3F1 mice. Urine samples were analyzed<br />

for HMB metabolites. To confirm these results and extend to human metab-<br />

390 SOT 2011 ANNUAL MEETING<br />

olism, in vitro studies were conducted by incubating 14C HMB with male and female<br />

liver hepatocytes from Sprague-Dawley rats, B6C3F1 mice, and humans.<br />

Samples were analyzed by LC-RAD and/or LC-MS/MS. <strong>The</strong>re were sex differences<br />

in the in vivo metabolism <strong>of</strong> HMB detected in urine between the male and female<br />

rat. <strong>The</strong> major metabolite in the female rat was not detected in the male rat.<br />

Similarly, the major metabolite in the male rat was a minor metabolite in the female<br />

rat. <strong>The</strong>re were also species differences between the rat and mouse, with the major<br />

metabolite in the male mouse urine present only in trace quantities in the male rat<br />

urine. Both HMB and 2,4-dihydroxy-benzophenone, which were present in the<br />

male mouse and rat urine, were absent or in trace quantities in the female rat urine.<br />

Species and sex differences in HMB metabolism were also observed in isolated rat,<br />

mouse and human hepatocytes. Female rodent hepatocytes produced all HMB-derived<br />

metabolites present in males, as well as a few minor metabolites not evident in<br />

males. Male human hepatocytes produced 10 HMB-derived metabolites compared<br />

to 8 detected in female human hepatocytes. <strong>The</strong> metabolites detected in these studies<br />

were primarily glucuronide and sulfate conjugates, but some Phase I oxidative<br />

intermediate metabolites were also observed. <strong>The</strong> in vitro data indicate that the<br />

mouse is a closer metabolic match to humans than the rat. (Work conducted under<br />

NIEHS contract N01-ES-75562).<br />

1823 THE IN VITRO METABOLISM OF METHYL AND<br />

PROPYL PARABENS IN HUMAN AND RAT.<br />

K. Choi, H. Joo, J. Campbell, M. Andersen and H. Clewell. <strong>The</strong> Hamner<br />

Institutes for Health Sciences, Research Triangle Park, NC.<br />

Parabens are antimicrobial preservatives widely used in cosmetic products and<br />

pharmaceuticals as well as in food and beverage processing. Methyl paraben (MP)<br />

and propyl paraben (PP) are the most predominantly used parabens. In mammals<br />

parabens are extensively hydrolyzed to p-hydroxy benzoic acid (pHBA) and further<br />

undergo phase II biotransformation via glucuronide, glycine and sulfate conjugation.<br />

However, their metabolism in humans has not been well characterized. We investigated<br />

the metabolism <strong>of</strong> MP and PP using subcellular fractions <strong>of</strong> various organs<br />

in human and rat. In human, pHBA was mainly produced in the liver,<br />

followed by the lung, skin, intestine and testis (for MP) or the intestine, kidney,<br />

lung, skin and testis (for PP). For MP in human, the velocities for pHBA production<br />

were 94.72±5.35 and 46.23±0.07 in liver microsomes and cytosol and<br />

38.17±3.64 and 13.11±0.45 (nmol mg protein-1 min-1) in lung microsomes and<br />

cytosol, respectively. For PP, the velocities for the production <strong>of</strong> pHBA were<br />

114.71±0.85 and 45.90±1.48 in liver microsomes and cytosol, 8.79±0.05 and<br />

32.38±5.50 (nmol/mg protein/ min) in intestine microsomes and cytosol, respectively.<br />

In rat liver microsomes, the velocities for the production <strong>of</strong> pHBA with treatment<br />

<strong>of</strong> MP and PP were 106.14±2.55 and 104.15±4.88 and in rat liver cytosol<br />

36.53±6.0 and 111.76±3.05 (nmol/mg protein/min), respectively. <strong>The</strong>se metabolism<br />

data provide key parameters for PBPK models that support cross-species extrapolation<br />

<strong>of</strong> parabens exposures.<br />

1824 PHASE II BIOTRANSFORMATION OF DI(2-<br />

EHTYLHEXYL) PHTHALATE IN HUMAN AND RAT.<br />

H. Joo 1 , K. Choi 1 , J. Grimes 1, 2 , T. O’Connell 1, 2 , R. Clewell 1 , J. Campbell 1<br />

and H. Clewell 1 . 1 <strong>The</strong> Hamner Institutes for Health Sciences, Research Triangle Park,<br />

NC and 2 <strong>The</strong> UNC, Chapel Hill, NC.<br />

In this study we demonstrated that three metabolites <strong>of</strong> di(2-ethylhexyl) phthalate<br />

(DEHP), mono(2-ethylhexyl) phthalate (MEHP), mono(2-ethyl-5-OH-hexyl) phthalate<br />

(5-OH MEHP) and mono(2-ethyl-5-oxo-hexyl) phthalate (5-oxo MEHP),<br />

were metabolized via conjugation with glucuronic acid in pooled human liver<br />

(HLM) and rat liver microsomes (RLM). Production <strong>of</strong> MEHP-, 5-OH MEHPand<br />

5-oxo MEHP glucuronide was measured by LC-ESI (-)/MS/MS. <strong>The</strong> metabolic<br />

rates in HLM and RLM were 37,460 ± 5,565 and 4,472 ± 206 for MEHP<br />

glucuronide, 102,229 ± 1,160 and 868 ± 3 for 5-OH MEHP glucuronide and<br />

5,549 ± 350 and 920 ± 28 (AUC mg protein-1 min-1) for 5-oxo MEHP glucuronide,<br />

respectively. We also determined metabolic activities <strong>of</strong> 12 human uridine<br />

5-diphosphoglucuronosyl transferase (UGT) is<strong>of</strong>orms (1A1, 1A3, 1A4, 1A6,<br />

1A7, 1A8, 1A9, 1A10, 2B4, 2B7, 2B15 and 2B17) toward MEHP, 5-OH MEHP<br />

and 5-oxo MEHP. Among the 12 UGTs 1A3, 1A8, 1A10, 2B7 and 2B17 were<br />

major is<strong>of</strong>orms for MEHP glucuronide production, while 1A3, 1A7, 1A8, 1A9,<br />

1A10 and 2B7 were mainly responsible for the production <strong>of</strong> 5-OH MEHP- and<br />

5-oxo MEHP glucuronide. <strong>The</strong> percent total normalized rates (%TNR) were 84%<br />

for MEHP glucuronide by UGT2B7 and 80% and 85% for 5-OH MEHP- and 5oxo<br />

MEHP glucuronide by UGT1A9, respectively. Additionally, we developed a<br />

method to biosynthesize milligram quantities <strong>of</strong> MEHP glucuronide for use as a<br />

reference standard. <strong>The</strong>se metabolism data are being used to support PBPK model<br />

evaluation <strong>of</strong> cross-species dosimetry and human interindividual variability for<br />

DEHP exposures.

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