Mammary Gland Whole Mount Round Robin Summary Suzanne Fenton, NIEHS, NTP December 4, 2009

Similar documents
Endocrine disruptors: Science for science's sake, science for health protection

SAB Report to the Board of the Glass Packaging Institute

DANIEL R. DOERGE U.S. Food and Drug Administration National Center for Toxicological Research Jefferson, AR

Evaluation of EFSA s new Scientific Opinion on Bisphenol A

DANIEL R. DOERGE U.S. Food and Drug Administration National Center for Toxicological Research Jefferson, AR

Weighing Evidence from National Toxicology Program Cancer Bioassays

Esposizione a livelli ambientali di xenoestrogeni: modelli di studio nel ratto in vivo e rilevanza degli effetti

Preparation of High-quality Hematoxylin and Eosin stained Sections from Rodent Mammary Gland Whole Mounts for Histopathologic Review

Endocrine Disrupting Activity Associated With Oil and Natural Gas Extraction

Consortium Linking Academic and Regulatory Insights on BPA Toxicity (CLARITY-BPA): Core Study

ANATOMICAL PATHOLOGY TARIFF

Exposure to Flaxseed or Purified Lignan During Lactation Influences Rat Mammary Gland Structures

ENDOCRINE DISRUPTORS: Endometriosis and Infertility

BREAST PATHOLOGY. Fibrocystic Changes

CLARITY-BPA: A Novel Approach to Studying Endocrine Disrupting Chemicals Retha Newbold

Sensitivity and Specificity of Bioassay of Estrogenicity on Mammary Gland and Uterus of Female Mice

FACT: FACT: Breast Cancer Staging. For cancer to occur, something must damage nucleus of the cell. Stage I. Stage II 10/9/2018

Endocrine Disrupting Chemicals: New considerations in the toxics space TURI Annual Meeting

Breast Pathology. Breast Development

The Role of E2Fs in Mouse Mammary Gland Development. A Senior Honors Thesis. April Sandy. The Ohio State University June 2006

To: National Toxicology Program (NTP); Center for the Evaluation of Risks to Human Reproduction (CERHR)

Status of Activities on BPA

EPA Health Advisory for PFOA and PFOS Drinking Water

Can Coatings Primer and Safety Assessment: Communicating Evidence of Absence

Breast Cancer and the Environment Research at NIEHS

Pathology Report Patient Companion Guide


Author's response to reviews

Neoplasia part I. Dr. Mohsen Dashti. Clinical Medicine & Pathology nd Lecture

A Cooperative (U01) Bisphenol A (BPA) Research Consortium Kembra Howdeshell, Ph.D.

Health Bites Breast Cancer. Breast Cancer. Normal breast

Diseases of the breast (1 of 2)

Endocrine Disruption and Human Health Effects

Mammary Nodular Hyperplasia in Intact R hesus Monkeys

Partial Results of NTP Chronic Carcinogenicity Studies of Cell Phone Radiofrequency Radiation in Rats

FSANZ Response to Studies Cited as Evidence that BPA may cause Adverse Effects in Humans

Bisphenol A (BPA) Affects Reproductive Formation across Generations in Mice

A712(18)- Test slide, Breast cancer tissues with corresponding normal tissues

Perfluorooctanesulfonic acid (PFOS) and Perfluorooctanoic acid (PFOA) What are PFOS and PFOA?

GOALS AND OBJECTIVES BREAST PATHOLOGY

Evaluation of Breast Specimens Removed by Needle Localization Technique

BPA Risk assessment work plan. Efsa, 29-30, October Jean Nicolas Ormsby (DER,anses)

Title: Scientific principles for the identification of endocrine disrupting chemicals a consensus statement

Breast pathology. 2nd Department of Pathology Semmelweis University

BREAST CANCER PATHOLOGY

Evaluation of Ramazzini Institute Aspartame Studies and EFSA s Assessment

Case study 1. Rie Horii, M.D., Ph.D. Division of Pathology Cancer Institute Hospital, Japanese Foundation for Cancer Research

Endocrine Disruptors Perspective of the Endocrine Society. R. Thomas Zoeller, Ph.D. Ana M. Soto, M.D.

CONTRIBUTED ARTICLES Weight of the Evidence Evaluation of Low-Dose Reproductive and Developmental Effects of Bisphenol A

NTP Toxicology and Carcinogenicity Studies of Cell Phone Radiofrequency Radiation

LYMPHATIC DRAINAGE AXILLARY (MOSTLY) INTERNAL MAMMARY SUPRACLAVICULAR

Your Guide to the Breast Cancer Pathology. Report. Key Questions. Here are important questions to be sure you understand, with your doctor s help:

A712(19)- Test slide, Breast cancer tissues with corresponding normal tissues

Quality ID #263: Preoperative Diagnosis of Breast Cancer National Quality Strategy Domain: Effective Clinical Care

A Testing Strategy for the Identification of mammalian Endocrine Disruptors with particular focus on steroids

Liver Disease NASH/Fibrosis Model

Large blocks in prostate and bladder pathology

Overview of US EPA Assessment Activities for Perfluorooctanoic Acid (PFOA) and Perfluorooctane Sulfonate (PFOS)

CLINICAL SIGNIFICANCE OF BENIGN EPITHELIAL CHANGES

Six Classes We can reduce harmful chemicals for a healthier world.

ICH Topic S1C(R2) Dose Selection for Carcinogenicity Studies of Pharmaceuticals. Step 5

Bisphenol A (BPA) in Plastics and Possible Human Health Effects

Science Policy Notice

Wellness Along the Cancer Journey: Cancer Types Revised October 2015 Chapter 2: Breast Cancer

Endocrine disrupters a role in human health?

Papillary Lesions of the breast

Low Dose Effects and Non-monotonic Dose Responses for Endocrine Active Chemicals: Science to Practice Workshop

CPC 4 Breast Cancer. Rochelle Harwood, a 35 year old sales assistant, presents to her GP because she has noticed a painless lump in her left breast.

Numbers behind Infographic Assuming Future is around 10 years from now For explanation of scaling see the end of the document CURRENT PREDICTIVE POWER

BREAST PATHOLOGY GROSSING GUIDELINES

Effects of perinatal exposure to BPA on obesity and metabolic disease later in life

Presented by: Lillian Erdahl, MD

Thermal Dermal Burn Modeling in Rats and Minipigs

Policy #: 120 Latest Review Date: June 2009

DOSE SELECTION FOR CARCINOGENICITY STUDIES OF PHARMACEUTICALS *)

BISPHENOL A: INFORMATION SHEET

S1.04 Principal clinician. G1.01 Comments. G2.01 *Specimen dimensions (prostate) S2.02 *Seminal vesicles

Justification Document for the Selection of a CoRAP Substance

Consideration of Reproductive/Developmental Mode of Action Data from Laboratory Animals in the Risk Assessment of Environmental Chemicals

Dose response relationships: biological and modeling aspects

5. Summary of Data Reported and Evaluation

of 3-Aminophenol in B6D2F1 Mice

Sheri Saluga A/P 2 May 1, Breast Cancer

Fertility and early embryonic development. Chris Willoughby, Huntingdon Life Sciences 11 October 2012

Exercise 6. Procedure

Exploring Environmental Chemicals and Risk of Breast Cancer During the Menopausal Transition

APPENDIX AVAILABLE ON THE HEI WEB SITE

p53 expression in invasive pancreatic adenocarcinoma and precursor lesions

Chapter 28. Breasts and Mammary Glands

Endocrine disruptors and effects on reproduction DEMETER: a support tool for occupational risks assessment

Breast Pedicle Protector

State of the Science Evaluation:

A case study in risk assessment: aspartame

Breast Cancer Task Force of the Greater Miami Valley A collaborative effort of health care professionals and breast cancer survivors in the Greater

Promise of a beautiful day

In the Name of God, the Most Merciful, the Most Compassionate. Breast

Effects of Endocrine Disruptors/Modulators on Fishes

Papillary Lesions of the Breast A Practical Approach to Diagnosis. (Arch Pathol Lab Med. 2016;140: ; doi: /arpa.

Contents 1 The Windows of Susceptibility to Breast Cancer 2 The So Called Pre-Neoplastic Lesions and Carcinoma In Situ

Inter-Laboratory Control Data for Reproductive Endpoints Required in the OPPTS / OECD 416 Reproduction and Fertility Test

Transcription:

Mammary Gland Whole Mount Round Robin Summary Suzanne Fenton, NIEHS, NTP December 4, 2009 In order to improve reliability and standardization of mammary gland whole mount assessments, directors and staff of seven laboratories from around the world (see attached) participated in a round robin evaluation of a set of mammary gland whole mounts. These preparations were from the 4 th and 5 th mammary glands of mice and rats treated in utero with vehicle and 2 different chemical treatments. Whole mounts were prepared from control and exposed mammary glands of female offspring at post-natal days 4, 21, and 45. The above-referred scientists, along with six other experts acting as observers, met to review their cumulative assessments and generate standardized guidelines for conducting mammary whole mount assessments. These methods and conclusions will be forthcoming as a scientific publication. At the meeting this group of scientists unanimously agreed on the following statements and have subsequently approved these written statements (finalized Dec. 4 th, 2009): Mammary gland whole mount preparations should be routinely incorporated into test protocols that include in utero or early life exposures in order to determine potential effects of chemicals on early life mammary gland development. Examples of protocols where this endpoint will likely be informative include the EPA Endocrine Disruptor Screening Program male and female pubertal protocols, and the extended one-generation reproductive toxicity assay currently under consideration by the EPA and OECD. Regarding study design and sample collection concensus was reached on the following: 1. The use of rodent mammary gland whole mounts will enhance the understanding of developmental effects, particularly during the pubertal period, of any test compound when exposure occured during prenatal or other early life period. Assessing effects by utilizing tissue sections alone is essentially a needle in the haystack approach, whereas the analysis of whole mounts allows for the detection of important developmental changes in the mammary gland that may not be identifiable in tissue sections. However, in aged rats, complementing the whole mount analysis with the histological approach may be necessary due to the thickness of the gland. Use of the data from histological analyses (collected from adult rodents) in combination with early life developmental end points in whole mounts should be informative of early life perturbations. These may lead to, or be correlated with, later life effects, particularly mammary cancer risk or impaired lactation. 2. Animal numbers must be based on power analyses. In our experience, and based on statistical analyses, single randomly selected pups from n=10-12 litters will produce the data needed to detect differences at the p<0.05 level. However, when testing at chemical exposure concentrations less than those used to determine the N, additional litters should be used in the study design to be sure that effects (or lack of effect) at low doses can be interpreted. 3. Litter size must be equalized at birth or soon after, keeping both male and female pups in the litter. Keeping male siblings is an important component to regulate female cyclicity, particularly in the mouse model. 1

4. Body weight of the animal should be measured just prior to the time of necropsy. This information should be used in statistical analyses, potentially as a covariate, when evaluating mammary gland end points. 5. Regulatory guidelines have proposed or set sample collection time points. If only one supplementary intermediate time point can be justified, PND 45 is recommended as collection time for mammary gland whole mounts of F1 and/or F2 offspring. The Round Robin evaluation session, across 7 laboratories, demonstrated a high degree of agreement at this time point, based on key developmental events at this stage of post-pubertal development. The following additional facultative collection times are also suggested: a. PND 4 Evaluation of mammary development at this time may reflect immediate effects of the compound of interest on mammary tissue, without significant effect by endogenous hormone changes. Culled pups should be used if litter equalization is performed on this day. b. PND 21 In rats, this time point would reflect another pre-pubertal time point with the added benefit of evaluating effects of lactationally distributed exposures on the mammary tissue, and without potentially confounding effects of cyclicity. In mice, this is the peri-pubertal period and important differences may be noted that are associated with pubertal timing.terminal end buds will be forming or have formed at this time. c. PND 90 Collection of mammary gland whole mounts, in addition to mammary tissue collected for histological sections, would be an asset, as preneoplastic lesions (ductal bridging, ductal carcinoma in situ, hyperplasia) can be detected at this time of life. Ideally, for histogical sections, the mammary gland and fat pad should be separated from the skin and placed in a cassette in toto. This will provide a histological specimen in frontal plane orientation in which the gland profile is comparable to the mammary whole mount. 6. Even though it is known that the thoracic mammary glands are among the first to form spontaneous or carcinogen-induced tumors, the 4 th and 5 th mammary glands of the mouse and rat, respectively, are the most easily accessible and reliable indicators of mammary developmental toxicants. 7. There are a variety of valid methods for mammary whole mount preparations, but the chosen method should include the following: a. The entire 4 th and 5 th (especially in the rat) gland should be utilized, with nipple(s) and lymph node present. b. The gland must be spread onto a surface of choice (e.g. charged glass slide, cloth, mesh, etc) and stretched, being careful to recapitulate the in situ size. c. The surface that the mammary gland is mounted onto should be larger than the gland. 8. The timing of vaginal opening (VO) should be determined in all studies in which mammary glands are collected. This is especially necessary when assessing PND 21 mouse mammary glands. 9. Because the stage of the estrous cycle is associated with subtle changes in mammary gland morphology in some (but not all) rodent strains, the stage of the estrous cycle should be determined on the day of necropsy (or by histopathology 2

later). If possible, compare mammary glands from animals morphologically determined to be in the same stage of the estrous cycle within and across treatment groups. Regarding mammary gland evaluations as a whole mount: 1. Mammary gland whole mounts should be captured as digital images and analyses performed via digital imaging when possible. Visual inspection of the entire gland does enhance interpretation of results. 2. The definition of terminal end buds in rats is teardrop-shaped ductal end structures that measure 100 µm or greater in diameter between the ages of birth and about 100 days. However, histological evaluation of any ends substantially larger than this size is recommended since that may be an indication of neoplastic change. 3. The definition of the terminal end bud in mice is nearly identical to that of the rat, except that the structure would measure 0.03 mm 2 or larger in area. 4. In order to evaluate developmental progression and to interpret the effects of treatment, the following parameters/end points/criteria should always be measured (quantitatively) in both rat and mouse mammary gland whole mounts: Terminal end bud number with respect to the number of other end types present. This should be done at all ages evaluated. (both before and after puberty, whether these values are normalized or not) Distance of epithelial outgrowth from the nipple toward the lymph node (for ages up to weaning) Distance from the lymph node to the end of longest extended duct (all post weaning end points) 5. Beyond the above stated similarities, the mouse and rat whole mounts are evaluated differently. The mouse whole mounts are evaluated as follows: Visually assess the relative amount of side branching, presence of lobules/alveoli, and duct thickness at all ages. Digitally assess branching density on both sides of the lymph node (ages beyond weaning), given that duct branching density is asymmetric and known to be greater closer to the nipple. Values on opposite sides of the lymph node are not comparable and should be analysed separately. 6. The rat whole mounts should be evaluated in the following ways: Visually assess budding, duct width, and differentiation from the lymph node to the outer edges. These differences from mouse measurements are required due to subtle but important differences in mammary gland development in the two species. Digitally assess the density in Area C if possible (outer 5 mm margin of the gland Russo and Russo, 1978. J Natl Cancer Inst 61:1451-1459). Consensus regarding the analyses of slides in the Mammary Gland Round Robin: 1. When compared to control glands, Treatment A caused significant changes in mouse mammary gland development. This was primarily due to the 5/7 and 7/7 labs finding significant effects in whole mounts of PND 21 and PND 45 F1 female offspring, respectively. 2. When compared to control glands, Treatment B induced significant changes in mouse mammary gland development. This is demonstrated by the 6/7 and 7/7 3

evaluators finding significant changes in whole mount analyses in F1 female offspring on PND 21 and PND 45, respectively. 3. Because 7 of 7 evaluating labs (in three separate countries) discovered statistically significant changes at PND 45, It was concluded that the glands were developmentally abnormal, raising concerns, and suggesting: a. An increased potential to develop intraductal hyperplasia, ductal bridging, or other preneoplastic conditions often present by PND 90. b. Altered potential for spontaneous tumor development. c. Altered susceptibility to chemical carcinogens or another exogenous insult. d. Potential for functional abnormality (inadequate lactation). e. Indication that endocrine disruption has occurred (other tissues should be evaluated for effects). 4. If developmental delays are noted, additional functional studies should be performed or other mammary time points collected and assessed to aid in interpreting results. 5. The rat mammary gland whole mounts that were not available at the time of the formal Round Robin will be assessed digitally (Fenton to photograph and put on a shared website). Other important conversations where consensus was not reached: 1. Choice of rodent strain: a. Inbred lines use of these strains may give more consistent outcomes due primarily to reduced variability between animals. Use of sensitive strains may allow the investigator(s) to evaluate specific susceptible subpopulations, but in many cases the relationship to human susceptible populations is not understood. Use of these lines may enable the investigator to reduce animal numbers (N=8-10), but that should be determined statistically. b. Outbred lines- use of these strains will more accurately represent the variability in the human population and will not specifically address any particular subpopulation. However, more animals are needed in these studies (N=10-12) to compensate for slightly higher variability. Outbred strains are also thought to be more consistent in their estrous cycle patterns than inbred strains. 2. Study confounders: a. Feed when testing a compound known to have estrogenic activity, it is recommended that a chow that is known to contain negligible amounts of xenoestrogens should be used. Acceptable examples include the purified formulations, AIN-76, AIN-93G or AIN-5K96. b. The study environment must be free of test compound contamination when testing a compound of unknown activity, the feed, water, dosing vehicle, bedding, cage material, and sample storage vials should be tested prior to beginning the study for contaminating levels of the test compound. These recommendations are particularly important for ubiquitous compounds, as has been shown critical for studies on bisphenol A or perfluorooctanoic acid. Furthermore, the phthalate field is known to have altered the general analytical reporting due to common environmental contamination of samples. 4

c. It is recommended that the test results from assays determining estrogenic activity in feed or environmental evaluations should be reported in resulting manuscripts. 3. Internal dose or compound half-life should be determined and reported. These data should be used to interpret effects on mammary tissue. These data should also be taken into consideration when choosing dose levels and length of exposure. 4. Mammary whole mount preparations: a. Removal different methods were discussed for removing the mammary gland for fixing the tissue. Some removed the entire mammary gland from the skin and mounted the tissue (fat pad), others removed the skin with the mammary gland intact for fixing. Both methods were viewed as adequate, and the method of choice would depend on the needs of the study and the skill of the technical staff performing the study. b. Staining 6 of 7 evaluating laboratories commonly use carmine as the stain of choice, although toluidine blue was noted as an excellent stain if careful attention is given to the ph of the stain. The presence of milk in the gland was reported to decrease the quality of toluidine staining. Toluidine blue stain allows better assessment of the stromal portion of the gland (e.g. inflammatory process and leucocytic infiltration to better detect progressing neoplasia) than carmine. An added advantage of working with carmine is that it autofluoresces when using confocal microscopy, a characteristic which has been shown to be useful in detecting tumors in various tissues (Huttenberger et al 2008; Betz et al, 1999; Anidjar et al 1998). c. Fixative the number of evaluating laboratories that use Carnoy s Fixative (ethanol, chloroform, glacial acetic acid; v 6:3:1) vs. buffered formalin as the fixing medium for mammary gland whole mounts was roughly equivalent. This choice will be left to the investigating lab, as both of these fixatives work well for early stage whole mounts. Carnoy s Fixative is the preferred choice for fatty tissues (older animals). d. Clearing agents - Xylenes and methyl salicylate were the clearing agents of choice. Methyl salicylate was preferred by the majority for clearing and long-term gland storage. Round Robin Participants: Sue Fenton, National Institute of Environmental Health Sciences Warren Foster, McMaster University Sandra Haslam, Michigan State University Leena Hilakivi-Clarke and Anni Warri, Georgetown University/University of Turku (Finland) Monica Munoz-de-Toro and Laura Kass, University of Litoral, Santa Fe, Argentina Jose and Irma Russo, Fox Chase Cancer Center Ana Soto and Carlos Sonnenschein, Tufts University Meeting Observers: Julie Boberg, Technical University of Denmark Daniel Desaulniers, Health Canada, Ottawa, Ontario 5

Susan Euling, US Environmental Protection Agency, NCEA John Latendresse, National Center for Toxicological Research Ruthann Rudel, Silent Spring Institute, Newton, MA Jason Stanko, Fenton Laboratory, NIEHS 6