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The Toxicologist - Society of Toxicology

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the observed CL values were 0.07 L/h in infants and ranged from 0.57 to 0.81 L/h<br />

in adults. In summary, clearance <strong>of</strong> ENB-0040 in humans was well predicted using<br />

this allometric modeling approach.<br />

1584 CHARACTERIZATION OF THE TRANSPORT AND<br />

INHIBITORY EFFECTS OF N-BUTYLPYRIDINIUM<br />

CHLORIDE AND ITS STRUCTURALLY RELATED<br />

IONIC LIQUIDS TO ROCT1/2.<br />

Y. Cheng 1 , S. Wright 2 , R. Kuester 1 , M. Hooth 3 and I. Sipes 1 . 1 Pharmacology,<br />

University <strong>of</strong> Arizona, Tucson, AZ, 2 Physiology, University <strong>of</strong> Arizona, Tucson, AZ<br />

and 3 NIEHS, Research Triangle Park, NC.<br />

Ionic liquids (ILs) are a class <strong>of</strong> salts <strong>of</strong>ten referred to “green chemicals”. <strong>The</strong>y are expected<br />

to be used as a new source <strong>of</strong> solvents and for many other applications. It has<br />

been shown previously that N-butylpyridinium chloride (NBuPy-Cl) was rapidly<br />

excreted in the rat kidney by glomerular filtration and renal secretion. This study investigated<br />

the role <strong>of</strong> the rat organic cation transporter 1 or 2 (rOCT1/2) in urinary<br />

secretion <strong>of</strong> ILs and their interaction with tetraethylammonium or metformin, substrates<br />

<strong>of</strong> rOCT1/2. After CHO cells stably expressing rOCT1/2 were constructed,<br />

transport <strong>of</strong> NBuPy-Cl, 1-methyl-3-butylimidazolium chloride (Bmim-Cl), and<br />

N-Butyl-N-methylpyrrolidinium chloride (BmPy-Cl) was characterized. <strong>The</strong> ability<br />

<strong>of</strong> NBuPy-Cl, Bmim-Cl, BmPy-Cl and alkyl substituted pyridinium to inhibit<br />

rOCT1/2 was also determined in vitro. NBuPy-Cl was infused to rats to assess its<br />

effect on the pharmacokinetics <strong>of</strong> metformin in vivo. NBuPy-Cl, Bmim-Cl and<br />

BmPy-Cl were all substrates <strong>of</strong> rOCT1/2 with K t<br />

values <strong>of</strong> 9/14 (rOCT1/2), 13/17<br />

and 277/43 μM, respectively. <strong>The</strong>y all exhibited strong inhibition to rOCT1/2<br />

(IC 50<br />

: 7.7~0.5 μM). <strong>The</strong> inhibitory effect <strong>of</strong> alkyl substituted pyridinium ILs increased<br />

(IC 50<br />

decreased) dramatically as the length <strong>of</strong> the side chain increases. <strong>The</strong><br />

IC 50<br />

values were 762, 72, 5, 2 μM (H-,C 2<br />

H 5<br />

-, C 4<br />

H 9<br />

-, C 6<br />

H 13<br />

- pyridinium chloride)<br />

for rOCT1 and 671, 14, 4, 0.1 μM for rOCT2. <strong>The</strong> in vivo co-administration<br />

study revealed that NBuPy-Cl decreased the elimination rate <strong>of</strong> metformin and<br />

therefore prolonged its plasma half-life in rats. <strong>The</strong>se results show that ILs are transported<br />

by rOCT1/2 and that they compete with other substrates <strong>of</strong> OCTs, which<br />

can alter the in vivo pharmacokinetics <strong>of</strong> such substrates. This research was supported<br />

by the NIEHS NTP Grant No. N01-ES-45529 and NIEHS-sponsored<br />

Southwest Environmental Health Science Center Grant Number P30-ES-06694.<br />

1585 COMPARATIVE PHARMACOKINETICS OF<br />

PERFLUOROHEXANESULFONATE (PFHXS) IN RATS<br />

AND MONKEYS.<br />

S. Chang 1 , D. J. Ehresman 1 , P. E. Noker 2 , G. W. Olsen 1 , G. S. Gorman 2 , J. A.<br />

Hart 1 , T. N. John 3 , M. Sundström 4 , Bergman 4 and J. L. Butenh<strong>of</strong>f 1 . 1 3M<br />

Company, St. Paul, MN, 2 Sourthern Research Institute, Birmingham, AL, 3 Pace<br />

Analytical Services, Minneapolis, MN and 4 Stockholm University, Stockholm,<br />

Netherlands.<br />

Perfluorohexanesulfonate (PFHxS) has been found in biological samples from<br />

wildlife and humans. <strong>The</strong> geometric mean half-life <strong>of</strong> serum elimination <strong>of</strong> PFHxS<br />

in humans has been estimated to be 7.3 years (95% CI 5.8-9.2 years). We undertook<br />

a series <strong>of</strong> studies to establish pharmacokinetic parameters in non-human<br />

species. Male (M) and female (F) monkeys were given a single intravenous (IV)<br />

dose <strong>of</strong> K + PFHxS and serum and urine PFHxS concentrations were followed for<br />

171 days. M and F rats were given single oral doses <strong>of</strong> 1, 10, or 100 mg/kg<br />

K + PFHxS and urine and feces were collected over 96 hours and serum and liver collected<br />

at 96 hours. Jugular-cannulated M and F rats were given either IV or oral<br />

single 10 mg/kg doses <strong>of</strong> K + PFHxS and serum concentrations <strong>of</strong> PFHxS were followed<br />

for 24 hours. M and F rats were given a single IV dose <strong>of</strong> 10 mg/kg, and<br />

serum, feces, and urine were collected weekly for 10 weeks. All PFHxS analyses utilized<br />

LC-MS/MS methods. Pharmacokinetic parameters were determined by<br />

WinNonlin® s<strong>of</strong>tware. Volumes <strong>of</strong> distribution indicated predominant extracellular<br />

distribution. Mean serum elimination half-lives were 141 and 87 days for M and<br />

F monkeys and ca. 30 and 1.5 days for M and F rats.<br />

1586 THE EFFECT OF COLESEVELAM HYDROCHLORIDE<br />

ON THE ELIMINATION OF POTASSIUM<br />

PERFLUOROOCTANOATE (PFOA) FROM SERUM IN<br />

MALE AND FEMALE CYNOMOLGUS MONKEYS.<br />

D. J. Ehresman 1 , P. E. Noker 2 , G. W. Olsen 1 , L. R. Zobel 1 , S. Chang 1 and J. L.<br />

Butenh<strong>of</strong>f 1 . 1 3M Company, St. Paul, MN and 2 Southern Research Institute,<br />

Birmingham, AL.<br />

Perfluorooctanoate (PFOA) is widely distributed in humans and wildlife. Due to its<br />

slow elimination in humans (serum geometric mean half-life (T 1/2<br />

)=3.5 yrs), this<br />

study was to evaluate whether colesevelam hydrochloride (colesevelam HCl, an<br />

anion-exchang resin compound that lowers lipids by impeding bile acid absorption<br />

in the intestine), can affect the elimination <strong>of</strong> PFOA from serum in cynomolgus<br />

monkeys. On study day (SD) 0, monkeys (N=3/sex/group, ~ 2 to 5 yrs old) received<br />

a single intravenous dose <strong>of</strong> K + PFOA (10 mg/kg)in cephalic vein. On SD<br />

21-27 and 56-83, daily oral doses <strong>of</strong> placebo (water) were given to Group 1 monkeys<br />

while Group 2 monkeys received placebo on SD 21-55. On SD 28-55, daily<br />

oral doses <strong>of</strong> colesevelam HCl (250 mg/kg-d) were given Group 1 monkeys while<br />

Group 2 monkeys received colesevelam HCl on SD 56-83. Serum samples were<br />

collected and analyzed for PFOA concentrations using LC/MS-MS from each<br />

monkey prior to dosing (0 hr), on SD 0 (0.5 hr post iv dose), 7, 14, 21, 28, 35, 42,<br />

49, 56, 63, 70, 77, and 84. All monkeys survived until the end <strong>of</strong> the study. <strong>The</strong>re<br />

were no clinically significantly abnormal observations noted and body weights were<br />

comparable between dose groups in each sex during the study. In either male (M)<br />

or female (F) monkeys, there was no apparent difference in mean serum PFOA levels<br />

between Group 1 (given colesevelam HCl on SD 28-55) and Group 2 (given<br />

colesevelam HCl on SD 56-83). PK parameters indicated similar mean overall<br />

serum half-life (T 1/2<br />

) and AUC values <strong>of</strong> PFOA in M monkeys in Group 1<br />

(T 1/2<br />

=18.8 days, AUC=1965 hrdμg/mL) and Group 2 (T 1/2<br />

=17.0 days,<br />

AUC=1716 hrdμg/mL); as well as in F monkeys in Group 1 (T 1/2<br />

=26.3 days,<br />

AUC=2869 hrdμg/mL) and Group 2 (T 1/2<br />

=28.4 days, AUC=2192 hrdμg/mL).<br />

<strong>The</strong>refore, administration <strong>of</strong> colesevelam HCl had no therapeutically significant<br />

impact on serum PFOA levels, serum PFOA half-life, or serum PFOA AUC levels<br />

within the limits <strong>of</strong> the study design.<br />

1587 ANALYTICAL METHOD VALIDATION OF N-BUTYL<br />

GLYCIDYL ETHER IN CORN OIL.<br />

J. W. Algaier 1 , D. M. Logan 1 , V. F. Ault 1 , O. L. Beverly 1 , A. Kazerooni 1 , B. M.<br />

O’Brien 1 , P. J. Schebler 1 , R. K. Harris 1 , B. Jayaram 2 and C. S. Smith 2 . 1 Energy<br />

and Life Sciences Division, Midwest Research Institute, Kansas City, MO and<br />

2<br />

National <strong>Toxicology</strong> Program, NIEHS, Research Triangle Park, NC.<br />

<strong>The</strong> compound n-Butyl Glycidyl ether (nBGE) is a high production volume chemical<br />

used in the production <strong>of</strong> epoxy resins. Epoxy resins are used in many commercial<br />

industries such as construction, electronics manufacturing and coating application.<br />

<strong>The</strong> ubiquitous presence <strong>of</strong> epoxy resins, and their components, in these<br />

industries has lead to concern for worker exposure. For this reason, nBGE has been<br />

selected for toxicological evaluation by the National <strong>Toxicology</strong> Program (NTP).<br />

An analytical method was developed and validated for the analysis <strong>of</strong> nBGE in corn<br />

oil to cover a dose formulation range <strong>of</strong> ~4.0 to ~100 mg/mL. Standards were prepared<br />

by adding nBGE and the internal standard (IS), 1-undecene, to corn oil and<br />

diluting the mixture with THF. <strong>The</strong> standards were analyzed using gas chromatography<br />

(GC) with flame ionization detection (FID) equipped with a Restek RTX-<br />

1701 (30 m x 0.53 mm I.D., 1.5-μm film thickness) column. <strong>The</strong> oven program<br />

was 40 °C (1-min hold) to 140 °C at 5 °C per minute and then to 240 °C at 20<br />

°C/min. <strong>The</strong> retention time was 12.4 min for nBGE and 13.0 min for the IS. <strong>The</strong><br />

method validation was linear (r ≥ 0.9999), accurate (from -0.8 to 0.9% relative<br />

error), and precise (% RSD ≤ 0.5). Following method validation a 42-day dose formulation<br />

stability study and a 3-hour simulated dosing study were performed at 10<br />

mg/mL nBGE in corn oil. <strong>The</strong> 42-day dose formulations were stored under ambient<br />

(25 °C) and refrigerated (5 °C) conditions. When compared to Day 0 values,<br />

the results indicated losses ≤ 0.6% under ambient conditions and ≤ 1.1% under refrigerated<br />

conditions. <strong>The</strong> 3-hour simulated dosing formulations were stored in<br />

clear serum vials exposed to air and light under ambient (25 °C) temperature. When<br />

compared to Day 0, the results indicated losses ≤ 0.6%. A high dose formulation <strong>of</strong><br />

~410 mg/mL nBGE in corn oil was evaluated for homogeneity and was shown to be<br />

homogeneous based on with an observed RSD <strong>of</strong> 0.7% for n=9 samples.<br />

1588 ANALYTICAL METHOD VALIDATION FOR THE<br />

QUANTITATION OF SIX NITROSAMINES IN NTP-2000<br />

RODENT FEED.<br />

P. J. Schebler 1 , A. D. Ammenhauser 1 , J. L. Cookinham 1 , J. W. Algaier 1 , R. K.<br />

Harris 1 , B. Jayaram 2 and C. S. Smith 2 . 1 Energy and Life Sciences Division, Midwest<br />

Research Institute, Kansas City, MO and 2 National <strong>Toxicology</strong> Program, NIEHS,<br />

Research Triangle Park, NC.<br />

Nitrosamines, a class <strong>of</strong> compounds identified as potentially carcinogenic, are<br />

found in beverages, nitrate cured foods and may be formed during cooking or food<br />

processing. <strong>The</strong> presence <strong>of</strong> nitrosamines in specialized rodent diets used for toxicology<br />

studies can potentially confound the interpretation <strong>of</strong> data from a toxicological<br />

study. Thus, it is important to demonstrate that rodent diets used in these studies<br />

are low in nitrosamines. To this end the National <strong>Toxicology</strong> Program has<br />

sponsored the development and validation <strong>of</strong> a chromatographic method to quantitate<br />

six nitrosamines (N-nitrosodimethylamine, N-nitrosodiethylamine, N-nitrosodibutylamine,<br />

N-nitrosopiperidine, N-nitrosopyrrolidine, and N-nitrosomorpholine)<br />

in NTP-2000 feed. Matrix standards covering a concentration range <strong>of</strong><br />

SOT 2010 ANNUAL MEETING 337

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