1 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 th e 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 W eight

- 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 f ocuse d 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 include s characterizing at what level of biological organization ( e.g ., molecular, cellular, tissue/organ, organism) that interaction is expressed

, the robustness of the data

s howing an interaction in terms of the extent of compl e mentarity and redundancy across multiple lines of evidence, and describing under what conditions ( e.g., in an organism with an intact hypothalamic

- pituita ry

- 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 W o E 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 hypothes e s and integrating data at different levels of biological or ganization

, which include s 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 ).2 

### Charge 1.

As described in the 2011 EDSP WoE guidance, i n assembling a n d 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 e nsure 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 clear ly 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 attain ing sufficiently high treatment doses/concentrations. Difficult to test substances may be encountered in Tier 1 scree n ing. Chemical S is an illustration of this situa tion. In the case of Chemical S

, consistent exposure was not achieved in the Amphibian Metamorphosis assay (AMA ) due to the physic al

- chemical characteristics of the test substance . The compound has low solubility and is highly lipophilic (high K ow ) and prone to sorbing to surfaces (high K oc )

. Due largely to these properties, the contributing laboratory performing the AMA with Chemical S did n ot achieve a concentration level high enough to produce a response indicative of a
maximum tolerated dose. Noneth eless, the agency concluded that the data were still useful in the WoE analysis

. This determination was based on the a gency’s understanding that while measured exposure concentrations were lower than the targeted nominal concentrations, exposure was reason ably quantified and that it is not likely that the chemical would be any less problematic to test if the study were repeated . Further, w hile 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 commen t on the agency’s conclusion regarding the utility of the AMA
data fo r Chemical S to still reliably evaluate its potential endocrine interaction in a WoE analysis.3 

### Charge 2.

The WoE guidance d ecision 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 characteriz ing the level of biological organization and the conditions under which potenti al endocrine interactions are expressed ( e.g., only in organisms with intact HPG or HPT axes, coin cid ent 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 non

endocrine pathways or mechanisms of pesticid al 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 s tudies 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 interaction s with E, A, or T signaling pathways. These case study analys e s 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 over t 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 it s pesticidal mode of action is cholinesterase inhibit i o n

. In particular, overt toxicity was observed at high concentrations in the FSTRA. Although a number of endocrine responses were observed ( e.g

. , decre ase 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 th e effects found at the high
concentration in the FSTRA may not necessarily be reflective of an endocrine

- mediated response, but rather a r eflection 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).4

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 con centration responses coincident with overt toxicity.

Charge 2.1.b. The pesticidal mode of action of Chemical S involves the uncoupli ng of mitochondrial oxidative phosphorylation and resulting in the depletion of ATP

. Another plausible mode of toxic ac tion 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 decrease d survival. The majority of potential androgen and estrogen

- related responses (decrease s in testosterone , decreases in male and female gonadal wei ghts

, delays in VO and PPS, decrease s 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 re sponses 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 pre sence 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.

P lease comment on how the agency’s has applied its decision logic to i ntegrat e 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 ov ert 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 stud y chemic als , 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 (decrease s in testosterone , decrease s in androgen sensitive tissue weights, delay s in PPS) near limit doses/concentrations (as described in the white pape r and test guidelines). However, a significant decrease in female VTG was observed at the intermediate dose.5

Observations of overt toxicity (decreased body weights and feeding) were reported in the highest treatment group ( i.e., near limit concentration s ) 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 . T he responses in fish and rats at the high dose could be due to a compromised metabolic abilit y 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 consider ed 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 illustrati on. 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 gonad al

- tissue or on fecundity). I n the case of Chemical A, the rat uterotrophic and female pubertal assay s ( i.e., an organism with an intact hypothalamic

- pituitary

- gonadal axis ) w ere negative for estrogen

- related response s , and a lthough there were som e response s in the FSTRA in the absence of overt toxicity

, th ey lacked diagnostic specificity ( e.g., effects on male gonadal tissue or GSI)

. Given the lack of comp l ementarity and redundancy in
responses within and across assays , the agency considered these situations as insufficient to support a robust conclusion o f an interaction with endocrine signaling pathways

.

Please comment on the decision logic the agency has used to characterize t hese 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 cont r ast to the situation described in question 2. 2.

, Chemical J appears to interact with the estrogen signaling pathway in terms of compl e mentarity and6

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 ., reduce d fecundity) in fish . However, this
biolo gical 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 conclusion s drawn. Please include in
your response, comments regarding the agency’s conclusion about differences in sens itivities 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 histolog y ). The a gency concluded that although there is evidence of a n 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 in teraction s of Chemical
A and the transparency and reasonable ness of th e 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 tha n what the in vitro assay evaluates or because an activated metabolite may be responsible for the in vivo effects. Chemical s 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

.7

For Chemical N, a nti

- 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 sensitiv e 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 response s 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., decrease s in testosterone levels) progressed to effects at the organ (tissue weight decreases in androgen
sensitive tiss ues) 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 re sponses 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, t here were T4 changes that were either marginal or equivoca l (Chemical A) , or isolated organ weight changes (Chemical s J and S) or histopathological changes of the thyroid gland (Chemical J) that were not coincident

w ith hormone changes. In the AMA , there were some isolated responses not necessarily indicative in terms of the endpoint specificity of a hypothalamic

- pituitary

thyroid 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

.8 

### 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 a nd include in your response the following points:

a. H ow consistent and transparent the cases studies are in terms of documentation.

b. H ow adequa tely the agency has described the extent of complementar it y and redundan cy 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. H ow the agency has used OSRI data to further characterize the obser vations from EDSP Tier 1 assays in determining potential chemical interactions with the E, A, and T signaling pathways

.