The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
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