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The Toxicologist - Society of Toxicology

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the antral follicles was monitored every 24h for a period <strong>of</strong> 96h. Further, we examined<br />

the gene expression levels <strong>of</strong> enzymes metabolizing MXC Cyp1a2, Cyp2c29<br />

and Cyp3a4 in the liver <strong>of</strong> ESR1 OE and control mice. Cyp1a2 and Cyp2c29 metabolize<br />

MXC, while Cyp3a4 metabolizes MOH and HPTE to their subsequent<br />

metabolites. <strong>The</strong> data show that at 96h, the cultured antral follicles from ESR1 OE<br />

antral follicles are more susceptible to toxicity induced by MXC, MOH and HPTE<br />

because low doses <strong>of</strong> these chemicals caused follicle growth inhibition in ESR1 OE<br />

mice, but not in control mice. In the livers, our results showed that while there was<br />

no difference in the mRNA levels <strong>of</strong> Cyp1a2 and Cyp2c29 between ESR1 OE and<br />

control livers, the mRNA levels <strong>of</strong> Cyp3a4 were significantly lower in ESR1 OE livers<br />

compared to controls (ESR1 OE fold-change over control = 1: Cyp1a2 = 1.2;<br />

Cyp2c29 = 1.1; *Cyp3a4 = 0.4; n = 5; *p ≤ 0.05). Collectively, these data suggest<br />

that ESR1 OE mice may be more susceptible to toxicity induced by MXC and its<br />

metabolites because <strong>of</strong> low clearance <strong>of</strong> the metabolites by the liver. Support: NIH<br />

R21ES13061, R01ES012893 and an Eli Lilly Fellowship in <strong>Toxicology</strong>.<br />

1039 MONO- AND DI-ESTER PHTHALATES ALTER<br />

TESTOSTERONE PRODUCTION IN MOUSE BLTK1<br />

MURINE LEYDIG TUMOR CELLS.<br />

Q. Ding 1 , N. A. Rahman 2 , I. T. Huhtaniemi 2 and T. R. Zacharewski 1 .<br />

1 Department <strong>of</strong> Biochemistry & Molecular Biology and Center for Integrative<br />

<strong>Toxicology</strong>, Michigan State University, East Lansing, MI and 2 Department <strong>of</strong><br />

Physiology, University <strong>of</strong> Turku, Turku, Finland.<br />

Phthalates, widely used plasticizers in a variety <strong>of</strong> consumer and industrial products,<br />

have been implicated in the etiology <strong>of</strong> rodent testicular dysgenesis by altering<br />

hormone levels. In this study, BLTK1 cells, a subclone <strong>of</strong> a murine Leydig cell line<br />

isolated from a testicular tumor in a inhibinα/SV40Tag transgenic mouse, are used<br />

to study the effects <strong>of</strong> phthalates and their monoester metabolites (i.e., DMP -<br />

mMP, DEP - mEP, DBP - mBP, BBzP - mBzP, DHP - mHP and DEHP - mEHP)<br />

on steroidogenesis. BLTK1 cells possess an intact steroidogenic pathway that produces<br />

low basal levels <strong>of</strong> progesterone (P) and testosterone (T) which is inducible<br />

by recombinant human chorionic gonadotropin (rhCG) as measured by ELISA.<br />

RT-PCR and western blot verified the expression <strong>of</strong> StAR, Cyp11a, Hsd3b1,<br />

Cyp17a1, Hsd17b3 in BLTK1 cells. rhCG (0.01 – 100 ng/ml) exhibited time- and<br />

dose-dependent induction <strong>of</strong> P and T levels with EC50 values <strong>of</strong> 1.8 and 1.5<br />

ng/ml, respectively, at 4 h. In rhCG time course studies, maximum P induction was<br />

achieved at 4 h, which returned to basal levels by 24 h while T levels gradually increased<br />

until 8 h and then remained relatively constant. mEHP also elicited marked<br />

time- and dose-dependent induction <strong>of</strong> P and T levels, while DBP, BBzP, and mHP<br />

induced moderate levels at 24 h. DMP, mMP, DEP, mEP, mBP, mBzP, DHP, and<br />

DEHP elicited negligible effects on P and T levels. QRT-PCR results indicate that<br />

mEHP exerts its effects by altering steroidogenic gene expression. More specifically,<br />

mEHP induced StAR mRNA levels while repressing the expression <strong>of</strong> Cyp17a1<br />

and Srd5a1. Overall, these results suggest that selected mono- and di-ester phthalates<br />

alter T biosynthesis by regulating the expression <strong>of</strong> specific steroidogenic<br />

genes. Partial funding was provided by the American Chemistry Council.<br />

1040 A STUDY OF FERTILITY IN SPRAGUE-DAWLEY RATS<br />

WITH XOMA 052, A NOVEL MONOCLONAL<br />

ANTIBODY TARGETING IL-1 BETA.<br />

C. Gasper 1 , B. Thorsrud 2 , J. Ma 1 , L. Cao 1 , K. Der 1 and K. Meyer 1 . 1 Product<br />

Development, XOMA (U.S. ) LLC, Berkeley, CA and 2 Developmental & Reproductive<br />

<strong>Toxicology</strong>, MPI Research, Mattawan, MI.<br />

XOMA 052 is an ultra-high affinity (300 fM) humanized IgG2 monoclonal antibody<br />

that specifically binds to IL-1 beta and inhibits activation <strong>of</strong> the IL-1 receptor.<br />

This activity is expected to prevent the cellular signaling events that produce inflammation<br />

associated with the development <strong>of</strong> diseases such as Type 2 diabetes,<br />

rheumatoid arthritis and Behçet’s disease. <strong>The</strong> rat was selected for this fertility study<br />

due to similar binding affinity and in vitro functional activity between human and<br />

rat IL-1 beta with XOMA 052. Male and female Sprague Dawley rats were administered<br />

XOMA 052 or vehicle by subcutaneous injection once weekly at dose levels<br />

<strong>of</strong> 0, 3, 30, and 90 mg/kg. Male rats were dosed weekly starting 28 days prior to<br />

pairing and continuing through euthanasia. Female rats were dosed weekly starting<br />

14 days prior to pairing until positive evidence <strong>of</strong> copulation was observed and<br />

again on GD 4. Mated females were each euthanized on GD 13 and all males were<br />

euthanized upon competition <strong>of</strong> the final GD 13 uterine examination.<br />

Observations and evaluations included clinical signs, gestation body weights and<br />

body weight change, food consumption, immunogenicity, macroscopic pathology,<br />

and reproductive performance (estrous cyclicity, reproductive and fertility indices,<br />

uterine and ovarian examinations, and sperm evaluation). All animals survived to<br />

scheduled necropsy. Results showed no toxicologically significant differences in any<br />

<strong>of</strong> the parameters evaluated. Based on the results, the no-observed-adverse-effect<br />

222 SOT 2011 ANNUAL MEETING<br />

level (NOAEL) for general and reproductive toxicity for male and female rats was<br />

considered to be 90 mg/kg, the highest dose level tested. In conclusion, XOMA<br />

052 was well tolerated and did not affect male or female fertility parameters or have<br />

any untoward effects during the period <strong>of</strong> early embryonic development to implantation<br />

in the rat.<br />

1041 IMMUNOHISTOCHEMICAL AND CHIP MICROARRAY<br />

ANALYSIS OF PPARα IN FETAL RAT TESTES EXPOSED<br />

TO DIBUTYLPHTHALATE (DBP).<br />

S. M. Plummer 1 , D. Dan 1 , J. Quinney 1 , M. Millar 3 , M. Sheila 3 , N. Hallmark 2 ,<br />

R. D. Phillips 2 and C. R. Elcombe 1 . 1 CXR Biosciences, Dundee, United Kingdom,<br />

2 ExxonMobil Petroleum & Chemical, Hermeslaan, Belgium and 3 MRC Human<br />

Reproductive Sciences Unit, Edinburgh, United Kingdom.<br />

Previous “ChIP on chip” studies indicated an increase in binding <strong>of</strong> peroxisome<br />

proliferator receptor alpha (PPARα) to the Cyp11a promoter in gestational day 15<br />

(GD15) rat testes could account for reduced Cyp 11a expression following DBP exposure<br />

(Plummer et al (2010) <strong>The</strong> <strong>Toxicologist</strong> CD, 114:1488). It was postulated<br />

that PPARα hinders transcription factor (SF-1) binding to the Cyp11a promoter,<br />

restricting Cyp11a expression and reducing testicular steroidogenesis. To test this<br />

hypothesis (1) ChIP microarray data analysis (GD15 and GD19 testes) on additional<br />

SF-1-regulated steroidogenic genes and (2) immunohistochemical staining<br />

(GD15 testes) for PPARα were conducted. ChIP microarray was performed (see<br />

ref. above) on GD15 and 19 fetal testes from Wistar rats exposed in utero to DBP<br />

(500mg/kg, p.o. to dams from GD12). Bouin’s fixed GD15 fetal testes were immunostained<br />

using antibodies against PPARα and 3βHSD, a Leydig cell marker.<br />

ChIP array data showed DBP increased PPARα binding in StAR and Cyp17a promoter<br />

regions in GD15 testes and inhibited SF1-binding in StAR and Cyp17a promoter<br />

regions in GD19 testes correlating with reduced expression <strong>of</strong> these SF-1regulated<br />

steroidogenic genes. Immunostaining results (GD 15) confirmed PPARα<br />

protein expression in interstitial regions <strong>of</strong> the testes partly colocalised with<br />

steroidogenic protein 3βHSD in Leydig cells. <strong>The</strong>se data are consistent with expression<br />

microarray data (Plummer et al (2007) Toxicol Sci 97:520) and suggest<br />

that DBP-induced alterations in PPARα binding could interfere with SF-1 binding<br />

in steroidogenic gene promoters. As PPARα is expressed primarily in immature<br />

Leydig cells it is likely that interference with SF-1 binding/ transactivation precedes<br />

functional maturity in target cells (3βHSD). <strong>The</strong> data are consistent with the hypothesis<br />

that PPARα could in part mediate DBP’s anti-androgenic effects. This<br />

work was supported by ExxonMobil Petroleum & Chemical<br />

1042 GESTATIONAL EXPOSURE TO ATRAZINE HAS LITTLE<br />

EFFECT ON FEMALE REPRODUCTIVE PARAMETERS<br />

IN SPRAGUE-DAWLEY (SD) RATS.<br />

L. K. Davis, A.S.Murr, T. E. Stoker, M. Narotsky, J. M. Goldman and R. L.<br />

Cooper. Endocrine <strong>Toxicology</strong> Branch, NHEERL, U.S. EPA, Research triangle pk, NC.<br />

Atrazine (ATR), a commonly used herbicide, has been shown to exert reproductive<br />

effects in animals; however, most <strong>of</strong> these studies have focused on adult exposure.<br />

In contrast, there is limited information available on the reproductive and developmental<br />

effects <strong>of</strong> gestational exposure to this herbicide. Here, we examined the effects<br />

<strong>of</strong> 0, 1, 5, 20 and 100 mg/kg ATR administered to SD dams on gestational<br />

days 14-21, a key developmental window, on female reproductive end points.<br />

Dosing occurred once daily or was divided into two doses per day; the lower doses<br />

were chosen based on existing female LOELs, while 100 mg/kg served as a positive<br />

control. 100 mg/kg decreased both maternal and <strong>of</strong>fspring body weights, and postnatal<br />

mortality was higher in this group shortly after birth. By postnatal day (PND)<br />

21 no differences in <strong>of</strong>fspring body weights were present. Age <strong>of</strong> vaginal opening,<br />

used as a pubertal index, was significantly delayed only in the 100 mg/kg group. No<br />

differences in body weights were seen at this time. Based on recently established<br />

guidelines, mammary gland whole mounts were prepared on PND 45 and analyzed<br />

by individuals blind to experimental treatment. <strong>The</strong>re were no apparent treatment<br />

effects on mammary gland development, including the number <strong>of</strong> terminal end<br />

buds and branch points. To determine the effects <strong>of</strong> gestational ATR exposure on<br />

estrous cycles in the adult <strong>of</strong>fspring, vaginal smears were examined until the control<br />

animals reached reproductive senescence (approximately 9 months). <strong>The</strong>se tracking<br />

data indicated that animals in the highest treatment group continued to cycle over<br />

this time, while growing numbers <strong>of</strong> females in the lower dose groups showed an<br />

emerging acyclicity. In brief, these data indicate that gestational exposure to ATR at<br />

doses as high as 100 mg/kg in the dam, had few adverse effects on these standard<br />

measures <strong>of</strong> reproductive development. This is an abstract <strong>of</strong> a proposed presentation<br />

and does not necessarily reflect EPA policy.

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