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The Toxicologist - Society of Toxicology

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males per group were dosed orally once daily from PND 22 to 42/43. <strong>The</strong> five<br />

groups in Set A were dosed with 0 mg/kg/day in corn oil, 25 or 100 mg/kg/day<br />

CN, and 30 or 60 mg/kg/day DE 71. <strong>The</strong> three groups in Set B were dosed with 0<br />

mg/kg/day in corn oil, and 12.5 or 50 mg/kg/day MET. Animals were examined<br />

for age and body weight at vaginal opening [VO] daily, beginning on PND 22; day<br />

<strong>of</strong> first estrous (DFE) and vaginal cytology. Necropsies were performed 2 hours<br />

post-dose on PND 42/43. Selected organs were weighed; ovaries, pituitary glands<br />

and thyroids were fixed for histological examination; and serum was collected for<br />

hormone analysis (thyroxine [T4] and thyroid-stimulating hormone [TSH]). <strong>The</strong>re<br />

were no clinical signs <strong>of</strong> toxicity or effects on feed consumption during the study.<br />

<strong>The</strong>re was a decrease in body weight and/or gain associated with CN and MET.<br />

Endocrine disruptive effects <strong>of</strong>: CN at 25 and/or 100 mg/kg/day included reduced<br />

organ weights <strong>of</strong> the ovaries and pituitary gland, a marked delay in VO and in the<br />

DFE, altered hypertrophic/hyperplasic uterine scores; decreased T4 and increased<br />

TSH. DE-71 at 30 and/or 60 mg/kg/day included reduced ovarian weight, increased<br />

thyroid weight; decreased thyroid colloid areas scores; decreased T4 and increased<br />

TSH; and delayed VO and DFE. MET at 12.5 and/or 50 mg/kg/day included<br />

reduced ovarian weight, advanced VO, irregular vaginal cytology (extended<br />

estrous). Conclusion: <strong>The</strong> applied experimental design satisfactorily detected the<br />

endocrine disruptive potential <strong>of</strong> the xenobiotics used in this validation.<br />

2111 MALE PUBERTAL ASSAY: VALIDATION USING KNOWN<br />

ENDOCRINE DISRUPTORS.<br />

R. M. Parker 1 , E. R. Frizell 1 , E. Horsley 2 and K. Hazelden 3 . 1 DART, Huntingdon<br />

Life Sciences, East Millstone, NJ, 2 Pfizer, Sandwich, United Kingdom and<br />

3<br />

MedImmune, Cambridge, United Kingdom.<br />

This study was performed to validate the ability <strong>of</strong> this assay to detect the endocrine<br />

disruptive potential <strong>of</strong> xenobiotics Vinclozolin (VN), DE 71, 1-Chloro-2-<br />

Nitrobenzene (CN) and Dibutyl Phthalate (DP) in pubertal male rats. Fourteen<br />

(Set A) and 15 (Set B) males per group were dosed orally once daily from PND 23<br />

to 52/53. <strong>The</strong> 5 groups in Set A were dosed with 0 mg/kg/day in corn oil, 30 or<br />

100 mg/kg/day VN, and 30 or 60 mg/kg/day DE 71. <strong>The</strong> 5 groups in Set B were<br />

dosed with 0 mg/kg/day in corn oil, 25 or 100 mg/kg/day CN, and 500 or 1000<br />

mg/kg/day DP. Rats were examined for preputial separation [PS] daily from PND<br />

30. Necropsies were done 2 hours post-dose on PND 52/53. Selected organs were<br />

weighed; testes, epididymides and thyroids were histologically evaluated; and serum<br />

was analyzed for hormones (thyroxine [T4], thyroid-stimulating hormone [TSH],<br />

and testosterone [T]). <strong>The</strong>re were no clinical signs <strong>of</strong> toxicity or effects on feed consumption.<br />

<strong>The</strong>re was a slight decrease in body weight gain from PND 23 to 52/53<br />

associated with DE 71 and VN. Endocrine disruptive effects <strong>of</strong>: DP at 500 and/or<br />

1000 mg/kg/day included decreased size and organ weights for the testis, epididymis<br />

and seminal vesicles (SV); reduced levator ani/bulbocavernosus [LABC]<br />

muscle weight; severe seminiferous tubule atrophy with totally depleted germ cells;<br />

reduced T4, TSH and T levels; and a delay in PS. VN at 30 and/or 100 mg/kg/day<br />

included reduced epididymis, SV, and LABC muscle and increased testis weights;<br />

reduced T4 and increased T levels; and a delay in PS. CN at 100 mg/kg/day included<br />

reduced ventral prostate, SV, LABC muscle; reduced TSH and increased T<br />

levels; and a delay in PS. DE 71 at 30 and/or 60 mg/kg/day included reduced<br />

LABC muscle and increased testis weights; reduced T4 and T and increased TSH<br />

levels; increased thyroid epithelial cell height, decreased colloid area; and a slightly<br />

delayed PS. Conclusion: <strong>The</strong> applied experimental design satisfactorily detected the<br />

endocrine disruptive potential <strong>of</strong> the xenobiotics used in this validation.<br />

2112 INTERACTION OF PERFLUOROALKYL ACIDS WITH<br />

HUMAN ESTROGEN RECEPTOR ALPHA.<br />

A. D. Benningh<strong>of</strong>f, D. Koch, W. Bisson, S. K. Kolluri and D. E. Williams.<br />

Environmental and Molecular <strong>Toxicology</strong>, Oregon State University, Corvallis, OR.<br />

Previously, we reported that multiple perfluoroalkyl acids (PFAAs) bind to the estrogen<br />

receptor (ER), induce expression <strong>of</strong> the estrogen biomarker protein vitellogenin<br />

and enhance liver carcinogenesis in rainbow trout, an animal model that<br />

represents the lack <strong>of</strong> sensitivity to peroxisome proliferators observed in humans.<br />

We now report new results from two studies examining the interaction <strong>of</strong> several<br />

PFAAs with human ERα. First, human embryonic kidney cells were transfected<br />

with the minimal SV40 promoter driving a luciferase gene containing the estrogen<br />

responsive element (ERE) and human ERα. Cells were then treated with estradiol<br />

(E2), perfluorooctanoic (PFOA), -nonanoic (PFNA), -decanoic (PFDA) and undecanoic<br />

(PFUnDA) acids as well as perfluorooctane sulfonate (PFOS) and 8:2 fluorotelomer<br />

alcohol (FtOH). PFOA, PFNA, PFDA and PFOS all significantly induced<br />

gene reporter activity up to 2.5-fold at concentrations ranging from 10 to<br />

1000 nM (PFOS increased reporter activity at 1 nM). PFUnDA and FtOH did not<br />

markedly alter gene reporter activity. Second, we employed a computational model<br />

using an iterative scoring method based upon 3D coordinates <strong>of</strong> the human ERα<br />

ligand binding domain complexed with E2 to investigate molecular docking <strong>of</strong><br />

these putative ligands with the receptor. PFOA, PFNA, PFDA and PFOS all efficiently<br />

docked with hERα and formed a hydrogen bond at residue Arg394, similar<br />

to other known xenogestrogens bisphenol A and nonylphenol. Interestingly, FtOH<br />

was found to effectively dock in this model similarly to the native hormone E2,<br />

which formed hydrogen bonds with both the Arg394 and Glu353 residues.<br />

PFUnDA did not interact with ERα in this computational model. <strong>The</strong>se data support<br />

the contention that several PFAAs may be xenoestrogens. Supported by NIH<br />

grants ES07060, ES03850 and ES00210.<br />

2113 THE ATRAZINE METABOLITE DACT CAUSES<br />

SUPPRESSION OF LH RELEASE IN LβT2 PITUITARY<br />

CELLS.<br />

A. C. Schell, R. B. Tjalkens, M. E. Legare and W. Hanneman. Colorado State<br />

University, Fort Collins, CO.<br />

Chlorotriazine (Cl-TRI) compounds such as atrazine (ATRA) are among the most<br />

commonly used herbicides worldwide. Exposure to ATRA and other Cl-TRIs<br />

causes a spectrum <strong>of</strong> reproductive and developmental deficits in laboratory species<br />

that involves selective disruption <strong>of</strong> the hypothalamic-pituitary gonadal (HPG) axis<br />

and blunting <strong>of</strong> the surge <strong>of</strong> leutinizing hormone (LH) from the pituitary gland induced<br />

by gonadotropin releasing hormone (GnRH). While this effect is well<br />

known, the mechanism <strong>of</strong> action by which the chlorotriazines blunt the LH surge<br />

is not known. Calcium is known to play a central role in the secretion <strong>of</strong> LH from<br />

the pituitary gonadotrophs. <strong>The</strong>refore, the objective <strong>of</strong> the present study was to elucidate<br />

if exposure to the atrazine metabolite diaminochlorotriazine (DACT) alters<br />

GnRH-induced intracellular Ca2+ release. LβT2 cells were treated for 24 hrs with<br />

300μM DACT and imaged for intracellular calcium utilizing the fluorescent probe<br />

Fluo-4 AM. Images were captured every 2 sec and 10nM GnRH was added at 30<br />

sec to stimulate intracellular Ca2+ release. Subsequent images were collected for 5<br />

minutes. DACT exposure resulted in a reduction in the GnRH-induced cytosolic<br />

Ca2+ transient. This decreased Ca2+ response correlated with loss <strong>of</strong> Ca2+ from<br />

thapsigargin-sensitive ER stores but could be recovered using the Ca2+ ionophore,<br />

A23187. Secretion <strong>of</strong> LH was also significantly reduced in DACT treated cells and<br />

was partially restored by treatment with A23187. <strong>The</strong>se results suggest that DACT<br />

directly targets G protein-coupled Ca2+ release signals in LβT2 cells to inhibit<br />

GnRH-stimulated release <strong>of</strong> LH.<br />

This work was supported by a grant from the College <strong>of</strong> Veterinary Medicine<br />

2114 A 28-DAY TOXICITY STUDY IN JUVENILE BEAGLE<br />

DOGS WITH A ONE MONTH RECOVERY FOLLOWING<br />

ORAL ADMINISTRATION OF FAROPENEM<br />

MEDOXOMIL.<br />

A. S. Faqi 1 , C. Lanphear 1 , S. Gill 2 and D. B. Colagiovanni 2 . 1 Developmental &<br />

Reproductive <strong>Toxicology</strong>, MPI Research, Mattawan, MI and 2 <strong>Toxicology</strong>, Replidyne,<br />

Inc., Louisville, CO.<br />

Faropenem Medoxomil (FM) is an orally active beta-lactam antibiotic belonging to<br />

the penem group which is being developed for community antibiotic use. <strong>The</strong> objective<br />

<strong>of</strong> this study was to determine the toxicity <strong>of</strong> FM when administered to<br />

neonatal/juvenile dogs for 28 consecutive days. <strong>The</strong> study consisted <strong>of</strong> a vehicle<br />

control and four treatment groups <strong>of</strong> five male and female dogs /group (2-3 weeks<br />

<strong>of</strong> age at study initiation). <strong>The</strong> treatment groups received FM at dose levels <strong>of</strong> 100,<br />

300, 600, or 1400 mg/kg/day (25, 75, 150, or 350 mg/kg/dose, respectively). FM<br />

or vehicle was administered to all groups via oral gavage, four times a day at a dose<br />

volume <strong>of</strong> 5 mL/kg/dose. Blood samples for clinical pathology evaluations were collected<br />

from all animals at pretest, during Week 2, and prior to the terminal (Week<br />

4) and recovery necropsies. Urine samples were collected from all animals prior to<br />

terminal and recovery necropsies via cystocentesis. TK samples were collected from<br />

all animals at designated time points on Days 1 and 27. Following 28 days <strong>of</strong> administration,<br />

two animals /sex at 0 and 1400 mg/kg/day were maintained for a 1<br />

month recovery period and then sacrificed with full necropsy. Body weight was significantly<br />

decreased in male puppies at 1400 mg/kg/day when compared to the<br />

control male animals. Comparison <strong>of</strong> Day 27 with Day 1 TK parameters showed a<br />

change in faropenem pharmacokinetic behavior over time with an apparent increase<br />

in the rate <strong>of</strong> clearance as observed in decrease in AUC0-6 with little to no<br />

change in Cmax and a decrease in Tmax values. Kidney lesions consisting <strong>of</strong> minimal<br />

to mild vacuolation and tubular degeneration/necrosis were observed at 1400<br />

mg/kg/day. Based on these results, the No Observed Adverse Effect Level<br />

(NOAEL) for general toxicity was 600 mg/kg/day based on kidney vacuolization<br />

and tubular degeneration/necrosis observed at 1400 mg/kg/day.<br />

SOT 2010 ANNUAL MEETING 449

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