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The Toxicologist - Society of Toxicology

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this class <strong>of</strong> drug would have few side effects because angiogenesis does not occur in<br />

adult, but an unanticipated toxicity has been hypertension (HTN) and proteinuria<br />

in 10 – 80% <strong>of</strong> patients receiving these drugs. It is now appreciated that these toxicities<br />

reflect inhibition <strong>of</strong> homeostatic VEGF signaling. In vasculature, VSP inhibition<br />

reduces VEGF-dependent nitric oxide levels, causing systemic vasoconstriction<br />

and HTN. In the kidney, podocyte-derived VEGF maintains glomerular endothelial<br />

cell health, and VSP inhibition induces glomerular endothelial damage, thrombotic<br />

microangiopathy and proteinuria. Intriguingly, patients developing grade 3 or<br />

4 HTN experience superior anti-tumor efficacy, suggesting that development <strong>of</strong><br />

HTN might be a useful pharmacodynamic marker <strong>of</strong> effective VSP inhibition. Two<br />

lessons can be drawn: First, in this era <strong>of</strong> targeted therapies, predicting toxicity from<br />

a specific and highly potent drug requires a thorough understanding <strong>of</strong> the drug<br />

target’s normal role in homeostasis. Rodent models allowing conditional gene inactivation<br />

in the adult will be increasingly required to predict these kinds <strong>of</strong> toxicities<br />

when knowledge <strong>of</strong> a signaling pathway’s role in normal physiology is incomplete,<br />

and several examples will be discussed. Second, because newer agents inhibit fewer<br />

targets, toxicities must be classified as either mechanism-dependent, or mechanismindependent<br />

(“<strong>of</strong>f-target”). Mechanism-dependent toxicities may in fact represent<br />

novel surrogate biomarkers <strong>of</strong> signal inhibition efficacy, such as HTN or proteinuria,<br />

to which drugs can be titrated in individual patients. Such a personalized dosing<br />

strategy may define the optimal therapeutic index for individuals, and perhaps<br />

help predict which patients are more likely to respond to a given agent.<br />

1444 LEAD OPTIMIZATION STRATEGIES AND NOVEL<br />

BIOMARKER TECHNOLOGIES TO ENSURE DRUG<br />

SAFETY.<br />

J. S. Ozer. Pharmacokinetics, Dynamics and Metabolism, Pfizer, Chesterfield, MO.<br />

Sponsor: S. Ramaiah.<br />

Because <strong>of</strong> the increased awareness and regulatory emphasis on drug safety issues<br />

during clinical trials and product post-marketing use, there is a need for newer biomarker<br />

technologies and approaches to better quantify and validate the most sensitive<br />

and specific safety biomarkers. Integration <strong>of</strong> multiple platform technologies<br />

including LC/MS/MS, LTQ-Orbitrap, ELISA, and Luminex is used to analytically<br />

and biologically validate safety biomarkers throughout drug development. Limiting<br />

antibody reagents across preclinical species for a particular assay can be overcome by<br />

employing MS technologies strategically. TFF3 is one safety biomarker for renal<br />

(urine) and GI (serum) injury where multiple platform technologies have been employed<br />

to analytically validate biomarker values. <strong>The</strong>se approaches and technologies<br />

can be applied during clinical trials and are feasible for translational use, whereas<br />

antibody technology shows limitations in cross-validations across species.<br />

Lead optimization approaches are employed to utilize safety biomarkers early in the<br />

pipeline using samples from discovery PK studies. Lead optimization allows chemistry<br />

support to be maximized in the pipeline, while screening for known toxicity liabilities.<br />

Prodromal renal functional markers <strong>of</strong> early organ toxicity are presented in<br />

a lead optimization format that is earlier than traditional histopathology endpoints.<br />

<strong>The</strong> renal model utilizes bile acids, leukotriene and proximal tuble enzymatic activity.<br />

It is critical that the biomarkers developed for use lead optimization are highly<br />

applicable to several preclinical models.<br />

1445 TOXICITY TESTING IN THE 21ST CENTURY FOR<br />

ECOTOXICOLOGY.<br />

S. Edwards 1 and G. T. Ankley 2 . 1 ORD/NHEERL, U.S. EPA, Research Triangle<br />

Park, NC and 2 ORD/NHEERL, U.S. EPA, Duluth, MN.<br />

<strong>The</strong> National Research Council (NRC) report, Toxicity Testing in the Twenty-first<br />

Century: A Vision and a Strategy has relevance for ecological as well as human<br />

health risk assessment. In April 2009, the <strong>Society</strong> <strong>of</strong> Environmental <strong>Toxicology</strong> and<br />

Chemistry (SETAC) held a workshop that considered key elements <strong>of</strong> the scientific<br />

foundation that would be needed to implement the vision <strong>of</strong> toxicity pathwaybased<br />

testing in support <strong>of</strong> ecological risk assessment <strong>The</strong> term adverse outcome<br />

pathway (AOP) was used to describe the linkage <strong>of</strong> molecular events modeled in a<br />

toxicity pathway assay to downstream biologic effects considered adverse from an<br />

ecotoxicological perspective (i.e., effects on survival, reproduction). Five challenges<br />

related to the elucidation and description <strong>of</strong> AOPs were considered. First, consistent<br />

with the NRC strategy concerning toxicity pathway elucidation and linkage to<br />

adversity, the challenge <strong>of</strong> describing AOPs from the extant literature and quantitatively<br />

modeling key components was addressed. Second, approaches for reverse engineering<br />

AOPs from combinations <strong>of</strong> transcriptomic, proteomic, metabolomic,<br />

and/or phenotypic data were examined. Because adversity in an ecological risk context<br />

is typically considered at the population level, approaches for translating toxicity<br />

pathway outputs into appropriate parameters for population modeling was a<br />

third challenge discussed. <strong>The</strong> fourth related to the challenge <strong>of</strong> discriminating<br />

adaptive (i.e., homeostatic, allostatic) responses from adverse ones and incorporating<br />

that knowledge into AOP models. Finally, because species extrapolation is a<br />

central challenge in ecological risk assessment, the workshop examined how to determine<br />

conservation <strong>of</strong> AOPs among species and use this information in predicting<br />

species sensitivity to support ecological risk assessments. This session will summarize<br />

the results <strong>of</strong> the SETAC effort and invite discussion with SOT members<br />

regarding development <strong>of</strong> an integrated toxicity testing paradigm that supports<br />

both human health and ecological risk assessment.<br />

1446 ADVERSE OUTCOME PATHWAY (AOP) MODELING OF<br />

KNOWN PATHWAYS.<br />

M. E. Andersen 1 , K. Watanabe 2 and I. R. Schultz 3 . 1 <strong>The</strong> Hamner Institutes,<br />

Research Triangle Park, NC, 2 Oregon Health and Science University School <strong>of</strong><br />

Medicine, Portland, OR and 3 Battelle Pacific Northwest, Sequim, WA.<br />

A nine-member workgroup representing disciplines <strong>of</strong> neurotoxicology, wildlife biology,<br />

ecotoxicology, and engineering developed a case study for domoic acid, an<br />

algal toxin with adverse effects on both wildlife and humans. <strong>The</strong> case study<br />

demonstrated strategies to develop computational models <strong>of</strong> known AOPs in an effort<br />

to move beyond the current toxicity testing paradigm focused on chemical-specific<br />

toxicity to a focus on toxicity pathway perturbations applicable for ecological<br />

risk assessment. Domoic acid is a potent agonist for kainate receptors - ionotropic<br />

glutamate receptors whose activation leads to the influx <strong>of</strong> sodium and calcium.<br />

Increasing intracellular calcium concentrations lead to toxicity and cell death. <strong>The</strong><br />

development <strong>of</strong> a conceptual framework for the AOP required an iterative process<br />

with two important outcomes: (1) a critically reviewed pathway from exposure to<br />

adverse outcome that is stressor specific and (2) identification <strong>of</strong> a key cellular<br />

process (or processes) suitable for evaluation in a mechanistic assay in vitro. <strong>The</strong><br />

toxicity pathway indicated that in vitro cellular assays <strong>of</strong> altered neuronal calcium<br />

should serve as a measure <strong>of</strong> the key response and that the results <strong>of</strong> these assays<br />

would be amenable to mechanistic modeling for identifying perturbations (and domoic<br />

acid treatments) that are within normal, those that are adaptive, and those<br />

that are clearly toxic. In vitro assays with outputs that are also amenable to measurement<br />

in exposed populations would link in vitro to in vivo conditions.<br />

Toxicokinetic information with domoic acid also aids in linking in vitro results to<br />

the individual. Another required step is taking projected responses <strong>of</strong> individuals<br />

and creating population models. All these linkages were considered in group considerations<br />

for the specific domoic acid example, leading to a series <strong>of</strong> more generic<br />

recommendations about strategies for literature mining and model development for<br />

known pathways.<br />

1447 REVERSE ENGINEERING ADVERSE OUTCOME<br />

PATHWAYS FROM ‘’OMICS DATA.<br />

E. J. Perkins 1 , K. Chipman 2 , F. Falciani 2 , S. Edwards 3 , T. Habib 4 , R. Taylor 5 ,<br />

G. Van Aggelen 6 , C. Vulpe 7 and N. V. Garcia-Reyero 8 . 1 Environmental<br />

Laboratory, U.S. Army ERDC, Vicksburg, MS, 2<br />

College <strong>of</strong> Life and Environmental<br />

Sciences, University <strong>of</strong> Birmingham, Birmingham, United Kingdom, 3<br />

NHRL, U.S.<br />

EPA, Research Triangle Park, NC, 4<br />

Biological Sciences, University <strong>of</strong> Southern<br />

Mississippi, Hattiesburg, MS, 5<br />

Systems Biology, Pacific Northwest National<br />

Laboratories, Richland, WA, 6<br />

Pacific Environmental Science Center, Environment<br />

Canada, Vancouver, BC, Canada, 7<br />

Nutritional Science and <strong>Toxicology</strong>, University <strong>of</strong><br />

California at Berkeley, Berkeley, CA and 8 Chemistry, Jackson State University,<br />

Jackson, MS.<br />

While many toxicologically-relevant pathways are known, many responses are mediated<br />

via unknown, or poorly characterized, mechanisms and modes <strong>of</strong> action.<br />

<strong>The</strong> advent <strong>of</strong> global analysis tools provides new capabilities for probing entire biological<br />

systems. Complex interaction networks can be reverse engineered or inferred<br />

from gene, protein, metabolic, signaling data enabling exploration <strong>of</strong> potential<br />

modes or mechanisms <strong>of</strong> toxic action. We describe reverse engineering <strong>of</strong> interaction<br />

networks from genes, proteins, and metabolites altered by toxicants to identify<br />

adverse outcome pathways in ecotoxicology. We then examined the utility <strong>of</strong> this<br />

for deducing toxicologically-relevant networks that regulate response to a defined<br />

stressor and dictate outcomes. A large data set <strong>of</strong> 868 arrays was used that focused<br />

on expression changes in fathead minnow ovary tissue representing exposure to 7<br />

different chemicals, over different times, and in vivo versus in vitro conditions. By<br />

applying different approaches, we demonstrate how this data set can be used to<br />

infer gene regulatory networks. <strong>The</strong> network path from stressor to adverse outcome<br />

can be considered a candidate adverse outcome pathway. Identification <strong>of</strong> candidate<br />

adverse outcome pathways allows for the formation <strong>of</strong> testable hypotheses about<br />

the key biologic processes, biomarkers or alternative endpoints, which could be<br />

used to monitor an adverse outcome pathway. Finally, we identify the unique challenges<br />

facing the application <strong>of</strong> this approach in this field, and attempt to provide a<br />

road map for the utilization <strong>of</strong> these tools<br />

306 SOT 2010 ANNUAL MEETING

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