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DATE: July 1, 2013

FIFRA Scientific Advisory Panel Meeting

July 30, 2013 - August 2, 2013

 Weight-of-Evidence: Evaluating Results of EDSP Tier 1 Screening

CHARGE QUESTIONS

Background:

The purpose of the current review is to seek comment from the FIFRA Scientific 

Advisory Panel (SAP) on the implementation of the basic interpretive process,

principles and concepts outlined in the agency’s 2011 EDSP Weight-of-Evidence (WoE) 

guidance (Appendix 1, see Section 3 of the white paper) as illustrated with case studies. 

The current case study analyses are primarily focused on the interpretative process for 

determining whether or not there is a chemical interaction with estrogen, androgen, or 

thyroid (E, A, or T) signaling pathways. An important aspect of addressing this question 

includes characterizing at what level of biological organization (e.g., molecular, cellular, 

tissue/organ, organism) that interaction is expressed, the robustness of the data 

showing an interaction in terms of the extent of complementarity and redundancy across 

multiple lines of evidence, and describing under what conditions (e.g., in an organism 

with an intact hypothalamic-pituitary-gonadal axis (HPG), in the absence of overt 

toxicity, at what doses, duration and route of exposure, etc.) the chemical interacts with 

and perturbs the endocrine system. 

The charge questions are organized around the fundamental steps in the WoE 

guidance (Section 3 of the white paper) in addressing whether or not a chemical 

interacts with the E, A, or T signaling pathways: (i) assembling and evaluating the 

scientific quality of the individual studies, and (ii) formulating hypotheses and integrating 

data at different levels of biological organization, which includes characterizing the 

extent and nature of the complementarity and redundancy in responses. In the context 

of these steps in the WoE guidance, cross-cutting as well as case study-specific 

questions are provided, consistent with the rationale for selecting the example 

chemicals for this review (see Section 4, Table 2 in the white paper).
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Charge 1.

As described in the 2011 EDSP WoE guidance, in assembling and evaluating the 

quality of scientific information to support a determination of a chemical’s potential to 

interact with E, A, or T signaling pathways, it is important to ensure data soundness, 

applicability, utility, clarity and completeness. 

Charge 1.1. Please comment on whether the agency has transparently described 

the conduct and results of the individual Tier 1 studies and the OSRI for each of 

the case studies (Sections 6-9 of the white paper), and specifically whether the 

level of detail is sufficient to ensure that a study is reliable for determining the 

potential to interact with E, A, or T signaling pathways and the rationale for the 

preliminary study conclusion.

Charge 1.2. For each of the case studies, please comment on whether the

performance criteria are clearly stated for the Tier 1 assays and, when results 

were not within the boundaries of the performance criteria, whether EPA has 

clearly expressed why the data are still considered reliable.

Charge 1.3. The test guidelines for Tier 1 assays recommend that the organism is 

challenged by attaining sufficiently high treatment doses/concentrations. Difficult to 

test substances may be encountered in Tier 1 screening. Chemical S is an illustration 

of this situation. In the case of Chemical S, consistent exposure was not achieved in 

the Amphibian Metamorphosis assay (AMA) due to the physical-chemical 

characteristics of the test substance. The compound has low solubility and is highly 

lipophilic (high Kow) and prone to sorbing to surfaces (high Koc). Due largely to these 

properties, the contributing laboratory performing the AMA with Chemical S did not 

achieve a concentration level high enough to produce a response indicative of a 

maximum tolerated dose. Nonetheless, the agency concluded that the data were still 

useful in the WoE analysis. This determination was based on the agency’s 

understanding that while measured exposure concentrations were lower than the 

targeted nominal concentrations, exposure was reasonably quantified and that it is not 

likely that the chemical would be any less problematic to test if the study were 

repeated. Further, while higher exposure concentrations could have been achieved in 

the AMA, the FSTRA indicates that these higher concentrations likely would have 

resulted in overt toxicity. 

Please comment on the agency’s conclusion regarding the utility of the AMA 

data for Chemical S to still reliably evaluate its potential endocrine interaction in 

a WoE analysis.
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Charge 2.

The WoE guidance decision framework is a hypothesis-based approach that promotes 

the analysis of effects at different levels of biological organization (molecular, cellular, 

tissue/organ, organism) using diverse in vitro and in vivo studies to determine whether

or not a chemical interacts with E, A, or T signaling pathways. Pivotal to this approach 

is the concept of adverse outcome pathways (AOP) or modes of action (MoA). All of the

case studies illustrate different data situations when characterizing the level of biological 

organization and the conditions under which potential endocrine interactions are 

expressed (e.g., only in organisms with intact HPG or HPT axes, coincident with overt 

toxicity, etc.) and varying degrees of complementarity and redundancy in responses 

encountered in the WoE analysis. 

Charge 2.1. Chemicals do not necessarily act by one adverse outcome pathway (AOP). 

The case studies provide an illustration of competing AOPs (endocrine versus nonendocrine pathways or mechanisms of pesticidal mode of action that lead to overt 

toxicity). Although it is important to ensure adequate dosing in studies and reach some 

level of toxicity, overt or pronounced toxicity was relatively common at high treatment 

doses/concentrations in the Tier 1 and OSRI studies in these case studies. When overt 

toxicity is observed in the Tier 1 in vivo assays, it is an important objective to integrate 

the understanding of overt toxicity in the context of the apical responses associated with 

potential chemical interactions with E, A, or T signaling pathways. These case study 

analyses include a characterization of the treatment-dependent nature and severity of 

the overt toxicity as well as the specificity of the potential endocrine-related responses 

coincident with the overt toxicity. These analyses inform the weight that is placed on 

certain Tier 1 responses in the presence of overt toxicity. The case studies provide 

illustrations of the different situations encountered. 

Charge 2.1.a. Chemical A can result in cholinergic toxicity given that its pesticidal 

mode of action is cholinesterase inhibition. In particular, overt toxicity was observed at 

high concentrations in the FSTRA. Although a number of endocrine responses were 

observed (e.g., decrease in female VTG, fecundity/fertility, GSI, male tubercles) at the 

highest concentration in the FSTRA, there was also pronounced overt toxicity that 

included abnormal behavior and significant body weight reductions consistent with 

cholinergic intoxication. Given the directionality of the FSTRA responses (i.e.,

decreases in the measured endpoints), EPA concluded that the effects found at the high 

concentration in the FSTRA may not necessarily be reflective of an endocrine-mediated 

response, but rather a reflection of a compromised organism with limited ability to 

maintain reproductive function and homeostasis. Although in male fish, overt toxicity 

was not observed at the intermediate concentration, possible endocrine responses were 

limited to two effects that lacked diagnostic specificity (i.e., altered GSI and histology). 
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Please comment on how the agency’s has applied its decision logic to integrate 

an understanding of overt toxicity in the context of observed Tier 1 in vivo 

responses , and in particular, the agency’s determination not to place weight on 

the FSTRA high concentration responses coincident with overt toxicity. 

Charge 2.1.b. The pesticidal mode of action of Chemical S involves the uncoupling of 

mitochondrial oxidative phosphorylation and resulting in the depletion of ATP. Another 

plausible mode of toxic action is related to its irritation properties including irritation that 

compromises the integrity of the gastro-intestinal tract in mammals leading to restricted 

caloric intake due to reduced food consumption. Reflective of these toxic modes of 

action, observations in the Tier 1 studies and OSRI included body weight reductions, 

behavioral effects, and decreased survival. The majority of potential androgen and 

estrogen-related responses (decreases in testosterone, decreases in male and female 

gonadal weights, delays in VO and PPS, decreases in male fertility, an increase in male 

GSI and VTG) were coincident with this overt toxicity. At concentrations where no 

apparent overt toxicity occurred, there were no endocrine related responses in the 

FSTRA, and responses in female rats were limited to a 2 day delay in VO, and for male 

rats, a decrease in the weights of two androgen-dependent tissues. The majority of 

Tier 1 responses were decreases in the measured endpoints, which were largely 

expressed in the presence of overt toxicity, are consistent with a depletion of ATP and 

restricted caloric intake. Although male VTG was increased in fish this is likely an 

artifact of a single elevated response. 

Please comment on how the agency’s has applied its decision logic to integrate

an understanding of overt toxicity in the context of observed Tier 1 in vivo

responses, and in particular, on the agency’s determination to place less weight 

on the Tier 1 in vivo responses in the presence of overt toxicity.

Charge 2.1.c. Chemical N is a cyclic unsaturated ketone whose acute mode of toxic 

action is nonpolar narcosis (toxicologically induced and reversible stages of neural 

disruption, i.e. general anesthesia). Unlike the other case study chemicals, there is no 

pesticidal mode of toxic action for N given that it is an inert ingredient. Testing required 

reaching limit doses/concentrations in order to sufficiently challenge the animal.

Potential androgen responses only occurred in the FSTRA (decrease female VTG, 

decrease fecundity/fertility, altered histology) and in the male pubertal assay (decreases

in testosterone, decreases in androgen sensitive tissue weights, delays in PPS) near 

limit doses/concentrations (as described in the white paper and test guidelines). 

However, a significant decrease in female VTG was observed at the intermediate dose. 
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Observations of overt toxicity (decreased body weights and feeding) were reported in 

the highest treatment group (i.e., near limit concentrations) in the FSTRA, but no overt 

toxicity was reported in the male pubertal assay. Unlike Chemicals A and S, the overt 

toxicity is not as pronounced for Chemical N. The responses in fish and rats at the high 

dose could be due to a compromised metabolic ability and inability to reduce chemical 

load. 

Please comment on the agency’s analysis in characterizing Tier 1 responses that

are expressed at or near limit doses where some degree of overt toxicity occurs, 

and the extent to which such responses are considered in the WoE analysis. 

Charge 2.1.d The case study analyses described above all involve situations in which 

overt toxicity was observed coincident with Tier 1 responses. 

Please comment on the agency’s overall approach to characterizing Tier 1

responses coincident with overt toxicity and determining the weight to be given 

to such responses. 

Charge 2.2. In certain case studies, there was a lack of anticipated complementary and 

redundant responses (within an in vivo assay or across assays) at different levels of 

biological organization (molecular, cellular, tissue/organ, and organism) indicative of a 

chemical interaction with an endocrine signaling pathway. The estrogen signaling 

pathway will be used as an illustration. In the case of Chemical N, the mammalian 

assays were negative and responses within the FSTRA did not progress to higher level 

responses (e.g., an effect on VTG did not translate to an effect on gonadal-tissue or on 

fecundity). In the case of Chemical A, the rat uterotrophic and female pubertal assays

(i.e., an organism with an intact hypothalamic-pituitary-gonadal axis) were negative for 

estrogen-related responses, and although there were some responses in the FSTRA in 

the absence of overt toxicity, they lacked diagnostic specificity (e.g., effects on male 

gonadal tissue or GSI). Given the lack of complementarity and redundancy in 

responses within and across assays, the agency considered these situations as 

insufficient to support a robust conclusion of an interaction with endocrine signaling 

pathways. 

Please comment on the decision logic the agency has used to characterize these 

types of situations where there is a lack of robustness in terms of 

complementarity and redundancy, and the transparency and reasonableness of 

the approach.

Charge 2.3. In contrast to the situation described in question 2.2., Chemical J appears 

to interact with the estrogen signaling pathway in terms of complementarity and 
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redundancy across multiple levels of biological organization as evidenced through 

altered steroidogenesis, resulting in decreased VTG in female fish which in turn 

translates to a higher-level response (e.g., reduced fecundity) in fish. However, this 

biological continuum was not observed in the Tier 1 rat female pubertal assays and the 

Part 158 mammalian data. 

Please comment on the how the agency has characterized this endocrine 

interaction at different levels of biological organization across taxa, and the 

transparency and reasonableness of the conclusions drawn. Please include in 

your response, comments regarding the agency’s conclusion about differences 

in sensitivities between taxa (i.e., fish and rats), regarding chemicals that appear 

to alter steroidogenesis.

Charge 2.4. Chemical A illustrates a situation where a molecular event has been 

initiated along a pathway via binding to the androgen receptor and by altered 

steroidogenesis, with corroborative evidence from the Hershberger assay. However, at 

a higher level of biological organization, an anti-androgenic response is not expressed

within the context of the mammalian intact hypothalamic-pituitary-gonadal axis (based 

on the Tier 1 mammalian assays and the mammalian in vivo OSRI). In the absence of 

overt toxicity, there were some possible endocrine-related responses in the FSTRA, but 

they lacked diagnostic specificity (e.g., reduced GSI and altered histology). The agency 

concluded that although there is evidence of an endocrine interaction (i.e., the androgen 

signaling pathway) at lower levels of biological organization, clear endocrine-driven 

responses are not expressed at higher levels of biological organization in organisms 

with an intact HPG-axis, presumably due to compensatory processes. 

Please comment on how the agency has integrated different sources of data 

along a biological continuum to characterize endocrine interactions of Chemical 

A and the transparency and reasonableness of the decision logic.

Charge 2.5. In some chemical situations, the in vitro Tier 1 data are negative. 

Nonetheless, this does not necessarily detract from a conclusion of a potential 

endocrine interaction in vivo either because a different molecular initiating event (MIE) 

may be occurring than what the in vitro assay evaluates or because an activated 

metabolite may be responsible for the in vivo effects. Chemicals N and S provide an 

illustration of this situation in that the MIE is uncertain due to the negative Tier 1 in vitro

assays. But, there were Tier 1 in vivo responses that are consistent with potential 

interactions with the androgen or estrogen signaling pathways. 
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For Chemical N, anti-androgen related responses were observed in the male pubertal 

assay that were complementary within the assay (i.e., decreased in testosterone levels 

that progressed to effects at the organ (tissue weight decreases in androgen sensitive 

tissues) and organism level (delay in PPS). In the FSTRA, more limited responses 

were observed in the absence of overt toxicity, i.e., a decrease in female VTG that did 

not manifest into higher level effects. In this case, there is in vivo evidence of an 

endocrine interaction but compared to other case studies (e.g., as Chemical J), the 

complementarity and redundancy in responses are not as robust. 

In the case of Chemical S for the A pathway, in the Hershberger there was a decrease 

in androgen-sensitive tissue weights. In the case of the male pubertal assay, there were 

complementary responses in that a cellular response (i.e., decreases in testosterone 

levels) progressed to effects at the organ (tissue weight decreases in androgen 

sensitive tissues) and organism level (delay in PPS). In the FSTRA, there were altered 

male gonadal weights and reduced tubercles. Although these effects in the fish lack 

specificity, they are supported by the mammalian responses. Tier 1 in vivo responses 

are not observed at the lower concentrations in organisms with an intact HPG-axis, 

presumably due to compensatory processes.

Please comment on the how the agency has integrated different sources of data 

along a biological continuum to characterize this endocrine interaction and the 

transparency and reasonableness of the conclusion drawn.

Charge 2.6. In each of the cases studies, there was a lack of anticipated 

complementary and redundant responses indicative of a chemical’s interaction with the 

thyroid signaling pathway. In the rat, there were T4 changes that were either marginal or 

equivocal (Chemical A), or isolated organ weight changes (Chemicals J and S) or 

histopathological changes of the thyroid gland (Chemical J) that were not coincident 

with hormone changes. In the AMA, there were some isolated responses not 

necessarily indicative in terms of the endpoint specificity of a hypothalamic-pituitarythyroid axis perturbation (Chemicals A and N). The agency considered the lack of 

complementarity and redundancy in responses to support a conclusion of no interaction 

with the HPT axis, and viewed these isolated responses insufficient to support a 

conclusion of an interaction with the thyroid signaling pathway.

Please comment on the how the agency has characterized this endocrine 

interaction at different levels of biological organization, and the transparency and 

reasonableness of the conclusion drawn.
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Charge 3.

Based on all of the case study analyses, please provide overall comments on how 

the agency has employed its WoE guidance and characterized the evidence and 

conclusions and include in your response the following points: 

a. How consistent and transparent the cases studies are in terms of 

documentation. 

b. How adequately the agency has described the extent of complementarity and 

redundancy of responses and has integrated and interpreted diverse lines of 

evidence across different biological levels of organization and taxa to reach 

preliminary conclusions regarding endocrine interactions. 

c. How the agency has used OSRI data to further characterize the observations 

from EDSP Tier 1 assays in determining potential chemical interactions with the 

E, A, and T signaling pathways.