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The Toxicologist - Society of Toxicology

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individuals. Week 6 results were quantifiable for 5/6 males with a mean <strong>of</strong> 46.28<br />

pg/mL, while 4/6 females had quantifiable results with a mean <strong>of</strong> 43.75 pg/mL.<br />

<strong>The</strong> last samples (Week 7 (fasted)) PTH values were quantifiable for all animals<br />

with means <strong>of</strong> 82.93 pg/mL and 57.38 pg/mL for males and females, respectively.<br />

Results below LLOQ were only obtained on the occasions when animals had access<br />

to food prior to blood sampling (Day 8 and Week 6), with lower means when compared<br />

to Day 1 and Week 7. In conclusion, increased PTH levels following a 7hour<br />

fasting period relative to the unfasted state provided more quantifiable and<br />

consistent values for data interpretation. This should be considered when developing<br />

a study design involving PTH assessment and, when possible, animals should<br />

be fasted prior to sampling.<br />

2377 EFFECTS OF ACUTE AND CHRONIC ALCOHOL<br />

EXPOSURE ON CELL SIGNALING IN BETA-<br />

ENDORPHIN (βEP) NEURONS OF THE<br />

HYPOTHALAMUS.<br />

L. Louis and S. Dipak. Rutgers University, New Brunswick, NJ.<br />

<strong>The</strong> endogenous opioid system is known to play a role in different aspects <strong>of</strong> alcohol<br />

addiction. Specifically, β-endorphin (β-EP) has long been suspected <strong>of</strong> making<br />

a major contribution to the positive reinforcement and motivational properties <strong>of</strong><br />

alcohol. Several studies have indicated that repeated administration <strong>of</strong> alcohol significantly<br />

attenuate β-EP expression in the hypothalamus and other various limbic<br />

areas, while acute administration <strong>of</strong> ethanol increases β-EP neurotransmission. In<br />

the rodent central nervous system, β-EP neurons are primarily located in the arcuate<br />

nucleus and the periarcuate area <strong>of</strong> the medial basal hypothalamus. β-EP produced<br />

in neurons in the arcuate area are derived from the pro-opiomelanocortin<br />

(POMC) peptide which also gives rise to several other peptides in these β-EP neurons<br />

including as alpha melanocyte stimulating hormone and adenocorticotropin<br />

hormone. <strong>The</strong> cellular mechanisms regulating POMC gene expression and subsequent<br />

β-EP expression under acute and chronic alcohol treatments have not been<br />

well characterized. Using immunohistochemical double staining techniques we<br />

demonstrate that changes in β-EP expression are affected by changes in the calcium<br />

dependant signaling molecules pCAMKII and its downstream molecules c-FOS<br />

and p-CREB after both acute and chronic alcohol treatments. Our findings<br />

demonstrate that under acute alcohol treatment β-EP expressing cells increase in<br />

the hypothalamus while β-EP producing neurons also increase the calcium dependant<br />

signaling molecules pCAMKII, pCREB and CFOS. However under chronic<br />

alcohol treatment β-EP expression in the hypothalamus decreases while β-EP neurons<br />

also expressing pCAMKII, pCREB and CFOS decrease in the hypothalamus.<br />

<strong>The</strong>se results give insight into the possible cell signaling molecules involved in the<br />

regulation <strong>of</strong> β-EP regulation in the arcuate area <strong>of</strong> the hypothalamus under the influences<br />

<strong>of</strong> acute and chronic alcohol exposure.<br />

2378 MIXTURES OF ANTI-ANDROGENS AT<br />

ENVIRONMENTALLY RELEVANT CONCENTRATIONS<br />

DISPLAY SIGNIFICANT ADVERSE EFFECTS ON<br />

HORMONES AND GENE EXPRESSION COMPARED TO<br />

SINGLE EXPOSURES AND THE CONTROL.<br />

J. P. Crago 1 and R. Klaper 2 . 1 Biological Sciences, University <strong>of</strong> Wisconsin-Milwaukee,<br />

Milwaukee, WI and 2 School <strong>of</strong> Freshwater Sciences, University <strong>of</strong> Wisconsin-<br />

Milwaukee, Milwaukee, WI. Sponsor: R. Hutz.<br />

Chemicals used by humans can enter into the aquatic environment through a variety<br />

<strong>of</strong> pathways. In some cases these chemicals have been shown to be potent agonists<br />

or antagonists <strong>of</strong> reproductive hormones. Most studies that examined exposures<br />

to these compounds look at single exposures and have no adverse effects on<br />

the organism at concentrations commonly found in the aquatic environment.<br />

<strong>The</strong>re have been few studies that examine the potential additive effects <strong>of</strong> mixtures<br />

at environmentally relevant concentrations, and specifically effects from compounds<br />

with the same adverse outcome but with different modes <strong>of</strong> action. <strong>The</strong><br />

goal <strong>of</strong> this study was to assess the effects <strong>of</strong> anti-androgenic mixtures versus individual<br />

anti-androgens on fish at concentrations commonly found in the aquatic environment.<br />

In this study male fathead minnows (Pimphales promelas) were exposed<br />

to the pesticide linuron (1ppb), di-ethylhexyl phthalate (DEHP) (12ppb), and in a<br />

mixture (linuron and DEHP) for a 28-day period. Gene expression pr<strong>of</strong>iles <strong>of</strong> the<br />

individual chemicals and chemical mixture were determined using cDNA microarrays<br />

followed by qRT-PCR were performed, and plasma testosterone concentrations<br />

and gonad-somatic index (GSI) were measured. <strong>The</strong> results from this study<br />

show that adverse effects were chemical dependent. Fish exposed to linuron showed<br />

a significantly lower GSI index as compared to control fish, DEHP treated fish, and<br />

fish treated to the mixture. Testosterone levels <strong>of</strong> fish treated with the mixture were<br />

significantly lower then that <strong>of</strong> the control, linuron and DEHP exposed fish. Genes<br />

involved in androgen production, such as cytochrome P450 17 and 11a did not differ<br />

amongst treatments, but alternate pathways were modified. <strong>The</strong>se results indicate<br />

that compounds shown to have anti-androgenic effects can have different adverse<br />

outcomes when combined in a mixture.<br />

2379 COMPARATIVE EVALUATION OF THE EFFECTS OF<br />

POLYBROMINATED DIPHENYLETHER (DE-71) AND<br />

ETHYLENE-BIS-TETRABROMOPHTHALIMDE (EBTBP)<br />

ON THYROID HORMONE-MEDIATED ANURAN<br />

METAMORPHOSIS.<br />

D. Fort 1 , R. Rogers 1 , P. Guiney 2 and J. Weeks 2 . 1 Fort Environmental Labs,<br />

Stillwater, OK and 2 S.C. Johnson & Sons, Racine, WI.<br />

An amphibian metamorphosis assay has been proposed by the US EPA in their Tier<br />

1 endocrine disruption screening program (EDSP). Previous studies suggested that<br />

the brominated flame retardant mixture, DE-71 impacts the function <strong>of</strong> the thyroid<br />

axis during metamorphosis in Xenopus laevis. Since brominated diphenylether<br />

(BDE) flame retardants are currently being replaced by a variety <strong>of</strong> alternative compounds,<br />

we compared the effects <strong>of</strong> a potential BDE replacement, ethylene-bistetrabromophthalimide<br />

(EBTBP), and DE-71 on thyroid-mediated metamorphosis.<br />

Tier 1 EDSP amphibian metamorphosis assays were conducted exposing stage<br />

51 X. laevis to 0.0, 0.4, 0.9, 2.1, and 3.8 μg/L DE-71 and 0.0, 4.4, 8.8, 17.5, and<br />

35 μg/L EBTBP from stage 51 for 21-d. Results from studies with DE-71 indicated<br />

that the rate <strong>of</strong> metamorphosis decreased with increasing concentration with no<br />

marked effect on thyroid gland histology. EBTBP exposure did not alter the rate <strong>of</strong><br />

metamorphosis or normal histology <strong>of</strong> the thyroid gland. Serum thyroxine (T4)<br />

and triiodothyronine (T3), thyroid gland T4, and thyroid hormone receptor beta<br />

(TRβ) expression in tail tissue were measured in stage matched larvae at the conclusion<br />

<strong>of</strong> exposure. Significantly lower levels <strong>of</strong> both T4 and T3 were measured in<br />

serum from DE-71 relative to controls, whereas no effect was observed in the<br />

EBTBP-treated larvae. Neither flame retardant significantly altered thyroid gland<br />

T4 level, nor altered the expression <strong>of</strong> TRβ. Thus, although DE-71 slowed metamorphosis<br />

by altering peripheral mechanisms <strong>of</strong> thyroid hormone homeostasis,<br />

EBTBP did not alter thyroid-mediated metamorphosis in X. laevis at environmentally<br />

relevant concentrations.<br />

2380 OECD VALIDATION STUDY ON THE<br />

TRANSFERABILITY, INTRA- AND INTER-LABORATORY<br />

REPRODUCIBILITY OF THE ZEBRAFISH EMBRYO<br />

TOXICITY TEST.<br />

F. Busquet 1 , S. Belanger 2 , T. Braunbeck 3 , G. Carr 2 , M. Halder 1 , A. Kleensang 1 ,<br />

A. Lillicrap 4 , S. Walter-Rohde 5 and P. Amc<strong>of</strong>f 6 . 1 JRC IHCP ECVAM, European<br />

Commission, Ispra, Italy, 2 Procter & Gamble, Cincinnati, OH, 3 University <strong>of</strong><br />

Heidelberg, Heidelberg, Germany, 4 NIVA, Oslo, Norway, 5 UBA, Dessau-Rosslau,<br />

Germany and 6 Environment, Health, and Safety Division, OECD, Paris, France.<br />

Sponsor: M. Embry.<br />

<strong>The</strong> OECD Acute Fish Toxicity Test Guideline (TG 203) is an integral component<br />

in the environmental safety assessment <strong>of</strong> industrial chemicals, agrochemicals,<br />

pharmaceuticals, feed stuffs, and biocides. One <strong>of</strong> the most promising alternative<br />

approaches to the acute fish toxicity test is based on the use <strong>of</strong> zebrafish embryos. In<br />

2005, the German Federal Environment Agency submitted the draft TG on “Fish<br />

embryo toxicity (FET) test” to the OECD Test Guideline Program and a supportive<br />

Background Paper. Subsequently, OECD established the ad hoc Expert Group<br />

on the Fish Embryo Toxicity Test. Based on the outcome <strong>of</strong> expert meetings,<br />

OECD decided to perform a validation study (coordinated by ECVAM and steered<br />

by a validation management group). <strong>The</strong> validation study aims to evaluate the<br />

transferability, and the intra/interlaboratory reproducibility <strong>of</strong> the Zebrafish FET<br />

(ZFET). Newly fertilised zebrafish eggs are exposed for up to 96h to chemicals. 4<br />

apical endpoints are recorded daily as indicators <strong>of</strong> acute lethality in fish: coagulation<br />

<strong>of</strong> the egg, lack <strong>of</strong> somite formation, non-detachment <strong>of</strong> the tail bud from the<br />

yolk sac and lack <strong>of</strong> heart-beat. LC50 values are calculated for 48h and 96h exposure.<br />

7 chemicals are tested at 5 different concentrations in 3 independent runs in<br />

at least 4 laboratories with appropriate controls. Stock solutions and test concentrations<br />

<strong>of</strong> 1 laboratory are confirmed. <strong>The</strong> poster will give an overview on the validation<br />

study design, the results, next steps and the correlation <strong>of</strong> the ZFET with acute<br />

fish LC50 data.<br />

“Disclaimer: <strong>The</strong> opinions expressed and the arguments employed herein are those<br />

<strong>of</strong> the authors and do not necessarily reflect the <strong>of</strong>ficial views <strong>of</strong> the OECD or <strong>of</strong><br />

the governments <strong>of</strong> its member countries’”<br />

SOT 2011 ANNUAL MEETING 511

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