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The Toxicologist - Society of Toxicology

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diated transcriptional response <strong>of</strong> all three ERs as compared to the two tandem<br />

EREs. PPT is not a specific agonist for the LMB ERα, as it also activates ERβ, and<br />

DPN was shown to activate the ERβs as well as the ERα. As expected, pp’-DDE<br />

and BPA were weak agonists <strong>of</strong> all three receptors. Dieldrin appears to be a more<br />

specific agonist <strong>of</strong> ERα, as it is not very efficacious in activating either ERβb or<br />

ERβa. <strong>The</strong> three LMB ERs showed different sensitivities to ICI 182,780, but at<br />

high concentrations (>5μM) it was able to completely inhibit the E2-mediated activation<br />

<strong>of</strong> all three ERs. Tissue slices from LMB livers will be used to test the effects<br />

<strong>of</strong> the above mentioned compounds on vtg synthesis.<br />

2358 IMPACT OF OSRI ON ANIMAL USE AND SCREENING<br />

BURDEN FOR TIER I EDSP COMPLIANCE.<br />

S. C. Gehen 1 and W. R. Jones 2 . 1 Dow AgroSciences, LLC, Indianapolis, IN and<br />

2 CropLife America, Washington, DC.<br />

In response to provisions <strong>of</strong> the Food Quality Protection Act (FQPA), EPA developed<br />

the endocrine disruptor screening program (EDSP) with the intent to identify<br />

chemicals that might interact with estrogen, androgen, or thyroid systems. In late<br />

2009, EDSP was implemented with receipt <strong>of</strong> testing orders for the chemicals on<br />

the first screening list, the majority being pesticide active ingredients. According to<br />

FQPA language and EPA policy, registrants can utilize existing toxicology information-<br />

or other scientifically relevant information (OSRI) - in lieu <strong>of</strong> generating new<br />

data for some or all tier I assays. This policy is especially noteworthy for pesticides<br />

where existing legislation mandates a comprehensive registration package <strong>of</strong> toxicology<br />

studies, several which assess endocrine-sensitive parameters. To evaluate the<br />

impact <strong>of</strong> OSRI on animal use and overall burden <strong>of</strong> endocrine screening, a retrospective<br />

analysis <strong>of</strong> registrant and EPA responses was conducted. Of the 58 individual<br />

pesticide registrants and consortia receiving testing orders, about 10% opted to<br />

voluntary cancel their respective EPA registration. Of those remaining, the degree<br />

to which registrants utilized OSRI was variable with 34% submitting OSRI for all<br />

11 tier I assays, 47% for a sub-set <strong>of</strong> tier I assays, and 9% choosing to conduct all<br />

11 assays. Registrants cited or submitted OSRI for a total <strong>of</strong> 211 (61%) in vivo<br />

EDSP studies; these responses ranged from 76% citing OSRI for the male pubertal<br />

assay to just 47% for the fish short-term reproduction assay. Of the first 5 test order<br />

responses published by EPA, registrants cited OSRI for 14 out <strong>of</strong> a possible 30 in<br />

vivo assays; however, none <strong>of</strong> these data-sets were considered sufficient by EPA to<br />

satisfy the test order, thus indicating that new in vivo studies would be required.<br />

Understanding the agency’s rationale for accepting or rejecting data submitted as<br />

OSRI will be increasingly important as this rationale directly affects animal use and<br />

the overall resource burden <strong>of</strong> the EDSP program.<br />

2359 ORAL EXPOSURE TO BISPHENOL A IMPACTS<br />

ELECTROCARDIOGRAPHIC PARAMETERS IN CD-1<br />

MICE.<br />

C. B. Lo, T. B. McCutchan, E. L. Kendig and S. M. Belcher. Pharmacology,<br />

University <strong>of</strong> Cincinnati, Cincinnati, OH.<br />

Bisphenol A (BPA) is an estrogenic endocrine disrupting chemical that is prevalent<br />

in the environment. Humans are exposed to significant amounts <strong>of</strong> BPA from the<br />

consumption <strong>of</strong> contaminated foods, beverages and other poorly defined routes.<br />

Our research has demonstrated that BPA can affect the cardiovascular system by altering<br />

intracellular Ca2+ handling in myocytes causing altered EC coupling and arrhythmias.<br />

<strong>The</strong> aim <strong>of</strong> this study was to determine whether oral exposure to estradiol<br />

or BPA can influence normal electrical function and rhythm <strong>of</strong> the heart in live<br />

CD1 mice. Male and female CD-1 mice were randomly paired following a two<br />

week pre-treatment period during which time animals were exposed to control diet<br />

or diet containing BPA (0.03, 0.3, 3, 30, and 300 ppm) or 17α-ethinyl estradiol<br />

(EE; 0.0001, 0.001, and 0.01 ppm). Treatments were continued through the life <strong>of</strong><br />

breeders (F0) and <strong>of</strong>fspring (F1). Electrocardiogram (ECG) data was collected and<br />

analyzed from conscious and unrestrained mice at different time points prior to<br />

mating, during pregnancy, and during <strong>of</strong>fspring development. Because levels <strong>of</strong> endogenous<br />

estrogen vary during the estrous cycle, the stage <strong>of</strong> estrous at time <strong>of</strong><br />

recording was determined. No significant differences in heart rate or other ECG<br />

parameters were observed during estrous in the control group. Dietary exposure to<br />

BPA (0.03 ppm and 0.3 ppm) and EE (0.01 ppm) caused significant effects on cardiovascular<br />

function during diestrus and estrus in CD-1 mice. <strong>The</strong> most efficacious<br />

dose <strong>of</strong> BPA was 0.3 ppm, while no effects have been observed at 30.0 ppm BPA. In<br />

F0 females 0.03 ppm BPA significantly increased heart rate and heart rate variability<br />

was suppressed in males. In the <strong>of</strong>fspring (F0), BPA (0.03 ppm and 0.3 ppm)<br />

and EE caused significant effects on cardiovascular function during diestrus and estrus.<br />

For these endpoints the most efficacious dose <strong>of</strong> BPA was 0.3 ppm, with no effects<br />

observed at 30.0 ppm BPA.<br />

2360 INTEGRATING HUMAN AND TOXICOLOGICAL<br />

EVIDENCE TO UNDERSTAND PCB EFFECTS ON THE<br />

DEVELOPING BRAIN.<br />

F. Parham 1 , A. Wise 2 , D. A. Axelrad 3 , K. Z. Guyton 3 , C. J. Portier 4 , L. Zeise 5 ,<br />

R. T. Zoeller 6 and T. J. Woodruff 2 . 1 National Institute for Environmental Health<br />

Science, Research Triangle Park, NC, 2 University <strong>of</strong> California, San Francisco, CA,<br />

3 U.S. EPA, Washington, DC, 4 Centers for Disease Control and Prevention, Atlanta,<br />

GA, 5 California EPA, Oakland, CA and 6 University <strong>of</strong> Massachusetts, Amherst, MA.<br />

We reviewed the relationships between chemical exposure, early biological disturbances,<br />

and subsequent overt health effects for thyroid hormone disruptions in a<br />

case study approach. Thyroid hormones (TH; thyroxine, T4 and triiodothyrine,<br />

T3) are essential for normal brain development and for normal physiological controls<br />

in adults. Mechanistic, laboratory animal, and human studies indicate that<br />

TH disruption during the prenatal period can cause permanent cognitive and neurobehavioral<br />

deficits. <strong>The</strong> quantitative relationships between TH disruption due to<br />

chemical exposures and overt disease were analyzed for polychlorinated biphenyls<br />

(PCBs). PCBs were chosen because sufficient animal and human data exist to<br />

model and compare body burdens, TH disruption and health decrements. We<br />

modeled three relationships following a review <strong>of</strong> 13 epidemiologic studies, applying<br />

meta-analysis where appropriate: 1) chemical exposures and TH changes; 2)<br />

pregnancy TH changes and neurodevelopmental outcomes <strong>of</strong> children; and 3) prenatal<br />

PCB exposures and neurodevelopmental outcomes <strong>of</strong> children. Using data<br />

from four chronic PCB studies in rats conducted by the National <strong>Toxicology</strong><br />

Program, we developed a low-dose linear model <strong>of</strong> PCB body burdens and T4 (free<br />

and total) decrements, accounting for 35 PCB congeners. A human extrapolation<br />

<strong>of</strong> the animal findings generally under-predicted the dose-response estimated from<br />

human studies. This quantitative analysis can inform approaches for evaluating<br />

human health consequences <strong>of</strong> exposures to multiple chemicals that exert thyroid<br />

toxicity.<br />

Disclaimer: <strong>The</strong> views expressed are those <strong>of</strong> the authors and do not necessarily represent<br />

the views and/or policies <strong>of</strong> the US EPA.<br />

2361 GENISTEIN NEGATES THE INHIBITORY EFFECTS OF<br />

LETROZOLE ON AROMATASE RELATED TO<br />

MALIGNANT, BUT NOT HEALTHY BREAST TISSUE.<br />

M. van Duursen 1 , E. de Morree 1 , S. Nijmeijer 1 , P. de Jong 2 and M. van den<br />

Berg 1 . 1 Institute for Risk Assessment Sciences, Utrecht University, Utrecht, Netherlands<br />

and 2 Department <strong>of</strong> Internal Medicine, St. Antonius Hospital, Nieuwegein,<br />

Netherlands.<br />

Aromatase (cytochrome P450 19, CYP19) catalyzes the conversion <strong>of</strong> androgens<br />

into estrogens. Especially in post-menopausal women, estrogen production in<br />

breast tissue by CYP19 becomes a major site <strong>of</strong> hormone production. In healthy<br />

breast adipose fibroblasts (BAF), CYP19 expression is low and is mainly driven by<br />

promoter I.4. In fibroblasts surrounding a tumor, a promoter switch to PI.3/II<br />

takes place and CYP19 expression is elevated 3-4-fold. This makes this enzyme an<br />

important target for estrogen-dependent breast cancer treatment by aromatase inhibitors,<br />

such as letrozole (LET). Breast cancer treatment <strong>of</strong>ten results in sudden<br />

onset <strong>of</strong> menopausal symptoms and many women seek for alternative therapies to<br />

treat these symptoms. A commonly used treatment is the soy-is<strong>of</strong>lavone genistein<br />

(GEN). In this study, the potential interaction between LET and GEN on CYP19<br />

was studied. In healthy primary human BAFs, PI.4-driven CYP19 expression was<br />

increased 45-fold by its stimulant dexamethasone. Expression <strong>of</strong> PI.3/II-driven aromatase<br />

was low in BAFs and only increased 7-fold by the stimulant PGE2. GEN<br />

did not affect CYP19 expression in BAFs. In contrast, in human adrenocorticocarcinoma<br />

H295R cells, that express PI.3/II-driven CYP19, GEN concentration-dependently<br />

induced aromatase activity (EC50=26 μM) and expression. LET inhibited<br />

CYP19 activity in H295R cells with an IC50 value <strong>of</strong> 0.2 μM. Co-incubation<br />

with GEN resulted in a concentration-dependent negation <strong>of</strong> CYP19 inhibition by<br />

LET through increased CYP19 expression. This interaction did not affect the<br />

EC50 <strong>of</strong> genistein, nor did it alter the IC50 <strong>of</strong> LET. <strong>The</strong>se data indicate that the actions<br />

<strong>of</strong> GEN on CYP19 appear to be restricted to PI.3/II-driven CYP19 that can<br />

be found in BAFs surrounding a tumor. <strong>The</strong>refore, the use <strong>of</strong> GEN by women undergoing<br />

breast cancer treatment with LET should be considered with care.<br />

2362 EFFECTS OF REDUCED-PHYTOESTROGEN DIETS ON<br />

DEVELOPMENT OF CD1 AND C57BL/6N MICE.<br />

E. L. Kendig, S. M. Christie, D. R. Buesing, C. K. Cookman, R. B. Gear, C.<br />

B. Lo and S. M. Belcher. Pharmacology, University <strong>of</strong> Cincinnati, Cincinnati, OH.<br />

Endocrine disrupting chemicals (EDC) are chemicals that can affect endocrine-dependent<br />

development and function. <strong>The</strong>se chemicals are prevalent in the environment<br />

and exhibit a variety <strong>of</strong> biological effects. Because <strong>of</strong> limited ability to replicate<br />

results from some animal studies controversy surrounds the possible harmful<br />

SOT 2011 ANNUAL MEETING 507

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