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The Toxicologist - Society of Toxicology

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17 BIOASSAY USE IN IDENTIFYING ENDOCRINE<br />

DISRUPTORS IN THE ENVIRONMENT.<br />

D. Schlenk. Environmental <strong>Toxicology</strong> Program, University <strong>of</strong> California Riverside,<br />

Riverside, CA.<br />

Advances in analytical chemistry have led to the detection <strong>of</strong> multiple chemical<br />

agents from numerous sources in surface waters around the globe. As such, the interactions<br />

<strong>of</strong> these mixtures continue to be an area <strong>of</strong> great uncertainty with regard<br />

to the potential risk <strong>of</strong> these “emerging” chemical agents to aquatic organisms, particularly<br />

extremely sensitive endocrine-specific responses. Using receptor-based<br />

models for estrogenic activity, strong correlations are observed with the occurrence<br />

<strong>of</strong> known estrogen receptor ligands and biological activity facilitating implementation<br />

<strong>of</strong> an EEQ approach based upon receptor additivity. However, when in vitro<br />

responses are partnered with in vivo activities, poor correlations are observed particularly<br />

in agricultural locations. Studies in the Central Valley <strong>of</strong> California using a<br />

combined approach <strong>of</strong> analytical chemistry with in vitro and in vivo bioassays for<br />

estrogenic activity in a Toxicity Identification Evaluation failed to identify concentrations<br />

<strong>of</strong> estrogen receptor ligands equivalent to either in vitro or in vivo EEQ values.<br />

Of more than a hundred analytes, only a few pesticides, alklyphenols (APs) and<br />

alkylphenol ethoxylates were detected in samples showing estrogenic activity. When<br />

detected compounds were administered in ambient concentrations as individual<br />

compounds, neither in vitro nor in vivo estrogenic activity was observed. However,<br />

when pesticides were combined with surfactants, similar EEQ values to those observed<br />

in field samples were observed in vivo, but not in vitro. Overall, these results<br />

indicate additivity-based models using in vitro methods may underestimate endocrine<br />

responses <strong>of</strong> mixtures in vivo, particularly when compounds have multiple<br />

targets along the hypothalamus-gonadal-pituitary axis (eg. APs).<br />

18 DIAGNOSTIC ASSESSMENT OF THE ECOLOGICAL<br />

RISK OF EDCS IN COMPLEX MIXTURES.<br />

G. Ankley. Med., NHEERL, ORD, U.S. EPA, Duluth, MN. Sponsor: L. Gray.<br />

Although it is important to be able to forecast the potential endocrine toxicity <strong>of</strong><br />

chemical mixtures that could enter aquatic environments, in many instances there<br />

is a need to determine possible effects <strong>of</strong> endocrine-active chemicals already present<br />

in complex environmental mixtures (e.g., effluents, sediments), as well as discern<br />

specific chemicals causing observed responses in exposed animals such as invertebrates,<br />

fish and amphibians. This presentation will focus on techniques to: (1) detect<br />

the occurrence <strong>of</strong> endocrine-active chemicals (e.g., estrogen and androgen receptor<br />

agonists) in complex aqueous samples using mechanism-based responses in<br />

cell lines or whole animals, (2) identify specific chemicals responsible for endocrine<br />

toxicity in complex mixtures through biologically-based fractionation procedures,<br />

and (3) use pathway-specific models to assess the potential for adverse effects <strong>of</strong><br />

chemical mixtures on individuals and populations. Case examples illustrating these<br />

approaches will focus on the effects <strong>of</strong> complex municipal, industrial or agricultural<br />

discharges, and chemical components <strong>of</strong> these wastes<br />

19 MOLECULAR ENDPOINTS AND MIXTURES OF<br />

ENDOCRINE DISRUPTING CHEMICALS IN FISH.<br />

N. D. Denslow 1 , N. Garcia-Reyero 2 , K. J. Kroll 1 , E. F. Orlando 3 , K. H.<br />

Watanabe 4 , M. S. Sepúlveda 5 , D. L. Villeneuve 6 , E. J. Perkins 7 and G. T.<br />

Ankley 6 . 1 Physiological Sciences, University <strong>of</strong> Florida, Gainesville, FL, 2 Chemistry,<br />

Jackson State University, Jackson, MS, 3 Animal and Avian Sciences, University <strong>of</strong><br />

Maryland, College Park, MD, 4 Division <strong>of</strong> Environmental and Biomolecular System,<br />

Oregon Health & Science University, Beaverton, OR, 5 Forestry and Natural<br />

Resources, Purdue University, West Lafayette, IN, 6 ORD, NHEERL, Med., U.S.<br />

EPA, Duluth, MN and 7 Environmental Laboratory, U.S. Army Engineer Research<br />

and Development Center, Vicksburg, MS.<br />

Microarray technology is a relatively novel tool in ecotoxicology and is beginning to<br />

be used for exposure and/or hazard characterization for ecological risk assessment.<br />

To develop a basis for this type <strong>of</strong> analysis, fathead minnows (Pimephales promelas)<br />

were treated with two binary mixtures: 17α-ethinylestradiol and the estrogen antagonist,<br />

ZM 189,154; and 17β-trenbolone (androgen) and the androgen antagonist,<br />

flutamide. Concentrations chosen were anchored to levels which affect cumulative<br />

egg production in 21-day fathead minnow reproduction assays. Unique gene<br />

expression fingerprints were identified in endocrine active tissues including brain,<br />

gonad and liver, which point to adverse outcome pathways. In the presence <strong>of</strong> excess<br />

antagonist, gene expression was reversed, but only for some genes, suggesting<br />

that the model compounds have additional activities beyond binding to soluble sex<br />

hormone receptors. Using the validated microarrays, effluents from water treatment<br />

plants and animal agricultural areas were tested. Expression pr<strong>of</strong>iles were unique at<br />

each <strong>of</strong> the locations, suggesting that they vary in their composition and complex-<br />

4 SOT 2011 ANNUAL MEETING<br />

ity. Expression changes in key genes such as steroidogenic acute regulatory protein<br />

(StAR) and estrogen receptors, among others illustrate the presence <strong>of</strong> endocrine<br />

disrupting chemicals. Pathway analysis illustrates toxicity pathways that may be <strong>of</strong><br />

importance for complex effluents.<br />

20 EFFECTS OF MIXTURES OF PHTHALATES,<br />

PESTICIDES, AND TCDD ON SEXUAL<br />

DIFFERENTIATON IN RATS: A RISK FRAMEWORK<br />

BASED UPON DISRUPTION OF COMMON<br />

DEVELOPING SYSTEMS.<br />

L. E. Gray. Reproductive <strong>Toxicology</strong> Branch, U.S. EPA, Research Triangle Park, NC.<br />

Since humans are exposed to more than one chemical at a time, concern has arisen<br />

about the effects <strong>of</strong> mixtures <strong>of</strong> chemicals on human reproduction and development.<br />

We are conducting studies to determine the 1) classes <strong>of</strong> chemicals that disrupt<br />

sexual differentiation via different mechanisms <strong>of</strong> toxicity, 2) effects associated<br />

with in utero phthalate, pesticide and 2,3,7,8 dioxin (TCDD) exposures, and 3)<br />

how mixtures <strong>of</strong> phthalates behave when combined with pesticides or TCDD. In<br />

the mixture studies, we have examined the postnatal development <strong>of</strong> male rat <strong>of</strong>fspring<br />

after in utero exposure to 1) pairs <strong>of</strong> AR antagonists, 2) pairs <strong>of</strong> phthalates,<br />

3) phthalates with AR antagonists, 4) five phthalates, 5) seven chemicals (four pesticides<br />

and three phthalates), 6) ten chemicals (four pesticides and six phthalates)<br />

and 7) the potent Ah receptor agonist TCDD plus a phthalate. We also have examined<br />

the effects <strong>of</strong> some <strong>of</strong> these chemicals on fetal male rat hormone levels and testicular<br />

gene expression levels. Results <strong>of</strong> these studies demonstrate that dose addition<br />

models generally provide the most accurate predictions <strong>of</strong> the observed effects<br />

<strong>of</strong> these mixtures on male rat sexual differentiation. For example, when ten chemicals<br />

were administered in utero, 100% <strong>of</strong> the males displayed reproductive tract<br />

malformations as predicted by dose addition models, whereas response addition<br />

models predicted that none <strong>of</strong> the males would be malformed. Our data indicate<br />

that cumulative risk assessments based upon disruption <strong>of</strong> common fetal targets or<br />

systems during development more accurately predicts mixture effects than does one<br />

based upon mechanisms <strong>of</strong> toxicity. This abstract does not necessarily reflect EPA<br />

policy. NTP, NIEHS/EPA Interagency Cooperative Research Agreement HHS Y1-<br />

ES-8014-01; EPA RW75922<br />

21 ESTROGENIC CHEMICAL MIXTURES AND<br />

ENDOGENOUS HORMONES – A ROLE IN BREAST<br />

CANCER DEVELOPMENT?<br />

A. Kortenkamp and E. Silva. Centre for <strong>Toxicology</strong>, <strong>The</strong> School <strong>of</strong> Pharmacy,<br />

University <strong>of</strong> London, London, United Kingdom. Sponsor: C. Rider.<br />

Elevated levels <strong>of</strong> endogenous steroidal estrogens have been linked to breast cancer<br />

risk, and there is good evidence that pharmaceutically administered steroids (for example<br />

as hormone replacement therapy) also play a role in the disease. <strong>The</strong> possible<br />

contribution <strong>of</strong> synthetic environmental estrogens remains controversial, in view <strong>of</strong><br />

their low potency compared with estradiol. To assess whether synthetic estrogens<br />

could conceivably add to the internal estrogenic load <strong>of</strong> women, we have conducted<br />

in vitro experiments with mixtures <strong>of</strong> steroidal, plant-derived and synthetic estrogenic<br />

chemicals. <strong>The</strong> agents were combined at the levels reported to occur in<br />

women’s serum, and assessed in the E-Screen assay. We found that the combined effects<br />

could be predicted accurately by using the concept <strong>of</strong> concentration addition.<br />

With extreme exposure scenarios similar to those encountered in certain areas <strong>of</strong><br />

South Europe, there was a significant added contribution <strong>of</strong> synthetic estrogens,<br />

over and above that <strong>of</strong> endogenous estrogens. Persistent organochlorine compounds<br />

such as p,p-DDE, frequently measured in breast cancer epidemiology studies,<br />

contributed little to an overall combination effect. <strong>The</strong> contribution <strong>of</strong> more<br />

polar phenolic chemicals, such as those used as UV-filter substances, was more pronounced.<br />

Our studies may help to prioritise chemicals for study in breast cancer<br />

epidemiology.<br />

22 ENVIRONMENTAL OXIDATIVE POLLUTANTS-<br />

INDUCED PULMONARY TOXICITY.<br />

L. L. Mantell 1 and J. T. Zelik<strong>of</strong>f 2 . 1 St. John’s University College <strong>of</strong> Pharmacy, Queens,<br />

NY and 2 New York University School <strong>of</strong> Medicine, Tuxedo, NY.<br />

Environmental oxidant toxicants remain a major public health concern in industrialized<br />

cities throughout the world. Population and epidemiological studies have associated<br />

oxidant air pollutant exposures with morbidity and mortality outcomes,<br />

and underscore the important detrimental effects <strong>of</strong> these pollutants on the lung. A

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