Matthew J. LeBaron
Dow Chemical Company
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Featured researches published by Matthew J. LeBaron.
Toxicological Sciences | 2012
Nicola Stagg; Matthew J. LeBaron; David L. Eisenbrandt; B. Bhaskar Gollapudi; James E. Klaunig
Oxyfluorfen is a herbicide that is not genotoxic and produces liver toxicity in rodents, following repeated administration at high dose levels. Lifetime rodent feeding studies reported in 1977 with low-purity oxyfluorfen (85%) showed no increase in any tumor type in rats (800 ppm, high dose) and only a marginally increased incidence of hepatocellular tumors in male CD-1 mice at the highest dose (200 ppm). To evaluate the potential carcinogenicity of the currently registered oxyfluorfen (> 98% purity), we conducted a series of short-term liver mode of action (MOA) toxicology studies in male CD-1 mice administered dietary doses of 0, 40, 200, 800, and 1600 ppm for durations of 3, 7, 10, or 28 days. MOA endpoints examined included liver weight, histopathology, cell proliferation, nuclear receptor-mediated gene expression, and other peroxisome proliferator-specific endpoints and their reversibility. Minimal liver effects were observed in mice administered doses at or below 200 ppm for up to 28 days. Increased liver weight, single-cell necrosis, cell proliferation, and peroxisomal acyl-CoA oxidase (ACO) were observed at 800 ppm after 28 days, but there was no increase in peroxisomes. Expression of Cyp2b10 and Cyp4a10 transcripts, markers of constitutive androstane receptor and peroxisome proliferator activated receptor α nuclear receptor activation, respectively, were increased at 800 and 1600 ppm after 3 or 10 days. Collectively, these data along with the negative genotoxicity demonstrate that oxyfluorfen (> 98% purity) has the potential to induce mouse liver tumors through a nongenotoxic, mitogenic MOA with a clear threshold and is not predicted to be carcinogenic in humans at relevant exposure levels.
Molecular Cancer | 2009
Zsuzsanna S. Nagy; Matthew J. LeBaron; Jeremy A. Ross; Abhisek Mitra; Hallgeir Rui; Robert A. Kirken
BackgroundSignal Transducer and Activator of Transcription 5 A and B (STAT5) are key survival factors in cells of the lymphoid lineage. Identification of novel, tissue-specific STAT5 regulated genes would advance the ability to combat diseases due to aberrant STAT5 signaling. In the present work a library of human STAT5 bound genomic elements was created and validated.ResultsOf several STAT5 responsive genomic regulatory elements identified, one was located within the first intron of the human BCL10 gene. Chromatin immuno-precipitation reactions confirmed constitutive in vivo STAT5 binding to this intronic fragment in various human lymphoid tumor cell lines. Interestingly, non-phosphorylated STAT5 was found in the nuclei of Kit225 and YT cells in the absence of cytokine stimulation that paralleled constitutive NFκB activation. Inhibition of the hyperactive JAK3/STAT5 pathway in MT-2 cells via the Mannich-base, NC1153, diminished the constitutive in vivo occupancy of BCL10-SBR by STAT5, reduced NFκB activity and BCL10 protein expression in a dose dependent manner. Moreover, depletion of STAT5 via selective antisense oligonucleotide treatment similarly resulted in decreased BCL10 mRNA and protein expression, cellular viability and impaired NFκB activity independent of IL-2.ConclusionThese results suggest that the NFκB regulator BCL10 is an IL-2-independent STAT5 target gene. These findings proffer a model in which un-activated STAT5 can regulate pathways critical for lymphoid cell survival and inhibitors that disrupt STAT5 function independent of tyrosine phosphorylation may be therapeutically effective in treating certain leukemias/lymphomas.
Toxicology Mechanisms and Methods | 2011
Reza J. Rasoulpour; Matthew J. LeBaron; Robert G. Ellis-Hutchings; Joanna Klapacz; B. Bhaskar Gollapudi
There has been a growing concern that epigenetic events, that is, heritable changes in gene expression superimposed on DNA nucleotide sequences, may be involved in chemically and/or nutritionally mediated adverse health outcomes, such as reproductive toxicity and cancer. This concern has been driven by an increasing number of studies reporting toxicant-induced alterations to the epigenome in the form of changes in DNA methylation, histone/chromatin remodeling, and altered expression of non-coding RNAs. These three major mechanisms of epigenetic modifications may have coordinated, independent, or potentially antagonistic influences on gene expression. Complicating this understanding is the incomplete understanding of the normal state and dynamic variation of the epigenome, which differs widely between cells, tissues, developmental state, age, strain, and species. This review serves as a framework to outline characteristics composing an ideal epigenetic screen(s) for hazard identification in product safety assessment. In order to implement such a screen, first there needs to be a better understanding of adaptive versus adverse changes in the epigenome, which includes identification of robust and reproducible causal links between epigenetic changes and adverse apical end points, and second development of improved reporter assay tools to monitor such changes. An ideal screen would be in vitro-based, medium- to high-throughput, and assess all three branches of epigenome control (i.e. methylation, histone modifications, non-coding RNAs), although also being quantitative, objective, portable (i.e. lab to lab), and relevant to humans.
Birth Defects Research Part B-developmental and Reproductive Toxicology | 2014
Christopher J. Borgert; Leah D. Stuchal; Ellen Mihaich; Richard A. Becker; Karin S. Bentley; John M. Brausch; Katie Coady; David R. Geter; Elliot Gordon; Patrick D. Guiney; Frederick G. Hess; Catherine M. Holmes; Matthew J. LeBaron; Steve Levine; Sue Marty; Sandeep Mukhi; Barbara H. Neal; Lisa Ortego; David Saltmiras; Suzanne I. Snajdr; Jane Staveley; Abraham Tobia
Weight of evidence (WoE) approaches are recommended for interpreting various toxicological data, but few systematic and transparent procedures exist. A hypothesis-based WoE framework was recently published focusing on the U.S. EPAs Tier 1 Endocrine Screening Battery (ESB) as an example. The framework recommends weighting each experimental endpoint according to its relevance for deciding eight hypotheses addressed by the ESB. Here we present detailed rationale for weighting the ESB endpoints according to three rank ordered categories and an interpretive process for using the rankings to reach WoE determinations. Rank 1 was assigned to in vivo endpoints that characterize the fundamental physiological actions for androgen, estrogen, and thyroid activities. Rank 1 endpoints are specific and sensitive for the hypothesis, interpretable without ancillary data, and rarely confounded by artifacts or nonspecific activity. Rank 2 endpoints are specific and interpretable for the hypothesis but less informative than Rank 1, often due to oversensitivity, inclusion of narrowly context-dependent components of the hormonal system (e.g., in vitro endpoints), or confounding by nonspecific activity. Rank 3 endpoints are relevant for the hypothesis but only corroborative of Ranks 1 and 2 endpoints. Rank 3 includes many apical in vivo endpoints that can be affected by systemic toxicity and nonhormonal activity. Although these relevance weight rankings (WREL ) necessarily involve professional judgment, their a priori derivation enhances transparency and renders WoE determinations amenable to methodological scrutiny according to basic scientific premises, characteristics that cannot be assured by processes in which the rationale for decisions is provided post hoc.
Toxicology and Applied Pharmacology | 2013
Matthew J. LeBaron; David R. Geter; Reza J. Rasoulpour; B. Bhaskar Gollapudi; Johnson Thomas; Jennifer Murray; H. Lynn Kan; Amanda J. Wood; Cliff Elcombe; Audrey Vardy; Jillian McEwan; Claire Terry; Richard Billington
Registration of new plant protection products (e.g., herbicide, insecticide, or fungicide) requires comprehensive mammalian toxicity evaluation including carcinogenicity studies in two species. The outcome of the carcinogenicity testing has a significant bearing on the overall human health risk assessment of the substance and, consequently, approved uses for different crops across geographies. In order to understand the relevance of a specific tumor finding to human health, a systematic, transparent, and hypothesis-driven mode of action (MoA) investigation is, appropriately, an expectation by the regulatory agencies. Here, we describe a novel approach of prospectively generating the MoA data by implementing additional end points to the standard guideline toxicity studies with sulfoxaflor, a molecule in development. This proactive MoA approach results in a more robust integration of molecular with apical end points while minimizing animal use. Sulfoxaflor, a molecule targeting sap-feeding insects, induced liver effects (increased liver weight due to hepatocellular hypertrophy) in an initial palatability probe study for selecting doses for subsequent repeat-dose dietary studies. This finding triggered the inclusion of dose-response investigations of the potential key events for rodent liver carcinogenesis, concurrent with the hazard assessment studies. As predicted, sulfoxaflor induced liver tumors in rats and mice in the bioassays. The MoA data available by the time of the carcinogenicity finding supported the conclusion that the carcinogenic potential of sulfoxaflor was due to CAR/PXR nuclear receptor activation with subsequent hepatocellular proliferation. This MoA was not considered to be relevant to humans as sulfoxaflor is unlikely to induce hepatocellular proliferation in humans and therefore would not be a human liver carcinogen.
Regulatory Toxicology and Pharmacology | 2013
Daland R. Juberg; Sean C. Gehen; Katie Coady; Matthew J. LeBaron; Vince Kramer; Haitian Lu; M. Sue Marty
Chlorpyrifos was selected for EPAs Endocrine Disruptor Screening Program (EDSP) based on widespread use and potential for human and environmental exposures. The purpose of the program is to screen chemicals for their potential to interact with the estrogen, androgen, or thyroid pathways. A battery of 11 assays was completed for chlorpyrifos in accordance with test guidelines developed for EDSP Tier 1 screening. To determine potential endocrine activity, a weight-of-evidence (WoE) evaluation was completed for chlorpyrifos, which included the integration of EDSP assay results with data from regulatory guideline studies and the published literature. This WoE approach was based on the OECD conceptual framework for testing and assessment of potential endocrine-disrupting chemicals and consisted of a systematic evaluation of data, progressing from simple to complex across multiple levels of biological organization. The conclusion of the WoE evaluation is that chlorpyrifos demonstrates no potential to interact with the estrogen, androgen, or thyroid pathways at doses below the dose levels that inhibit cholinesterase. Therefore, regulatory exposure limits for chlorpyrifos, which are based on cholinesterase inhibition, are sufficient to protect against potential endocrine alterations. Based on the results of this WoE evaluation, there is no scientific justification for pursuing additional endocrine testing for chlorpyrifos.
Environmental and Molecular Mutagenesis | 2017
Kerry L. Dearfield; B. Bhaskar Gollapudi; Jeffrey C. Bemis; R. Daniel Benz; George R. Douglas; Rosalie K. Elespuru; George E. Johnson; David Kirkland; Matthew J. LeBaron; Albert P. Li; Francesco Marchetti; Lynn H. Pottenger; Emiel Rorije; Jennifer Y. Tanir; Véronique Thybaud; Jan van Benthem; Carole L. Yauk; Errol Zeiger; Mirjam Luijten
For several decades, regulatory testing schemes for genetic damage have been standardized where the tests being utilized examined mutations and structural and numerical chromosomal damage. This has served the genetic toxicity community well when most of the substances being tested were amenable to such assays. The outcome from this testing is usually a dichotomous (yes/no) evaluation of test results, and in many instances, the information is only used to determine whether a substance has carcinogenic potential or not. Over the same time period, mechanisms and modes of action (MOAs) that elucidate a wider range of genomic damage involved in many adverse health outcomes have been recognized. In addition, a paradigm shift in applied genetic toxicology is moving the field toward a more quantitative dose‐response analysis and point‐of‐departure (PoD) determination with a focus on risks to exposed humans. This is directing emphasis on genomic damage that is likely to induce changes associated with a variety of adverse health outcomes. This paradigm shift is moving the testing emphasis for genetic damage from a hazard identification only evaluation to a more comprehensive risk assessment approach that provides more insightful information for decision makers regarding the potential risk of genetic damage to exposed humans. To enable this broader context for examining genetic damage, a next generation testing strategy needs to take into account a broader, more flexible approach to testing, and ultimately modeling, of genomic damage as it relates to human exposure. This is consistent with the larger risk assessment context being used in regulatory decision making. As presented here, this flexible approach for examining genomic damage focuses on testing for relevant genomic effects that can be, as best as possible, associated with an adverse health effect. The most desired linkage for risk to humans would be changes in loci associated with human diseases, whether in somatic or germ cells. The outline of a flexible approach and associated considerations are presented in a series of nine steps, some of which can occur in parallel, which was developed through a collaborative effort by leading genetic toxicologists from academia, government, and industry through the International Life Sciences Institute (ILSI) Health and Environmental Sciences Institute (HESI) Genetic Toxicology Technical Committee (GTTC). The ultimate goal is to provide quantitative data to model the potential risk levels of substances, which induce genomic damage contributing to human adverse health outcomes. Any good risk assessment begins with asking the appropriate risk management questions in a planning and scoping effort. This step sets up the problem to be addressed (e.g., broadly, does genomic damage need to be addressed, and if so, how to proceed). The next two steps assemble what is known about the problem by building a knowledge base about the substance of concern and developing a rational biological argument for why testing for genomic damage is needed or not. By focusing on the risk management problem and potential genomic damage of concern, the next step of assay(s) selection takes place. The work‐up of the problem during the earlier steps provides the insight to which assays would most likely produce the most meaningful data. This discussion does not detail the wide range of genomic damage tests available, but points to types of testing systems that can be very useful. Once the assays are performed and analyzed, the relevant data sets are selected for modeling potential risk. From this point on, the data are evaluated and modeled as they are for any other toxicology endpoint. Any observed genomic damage/effects (or genetic event(s)) can be modeled via a dose‐response analysis and determination of an estimated PoD. When a quantitative risk analysis is needed for decision making, a parallel exposure assessment effort is performed (exposure assessment is not detailed here as this is not the focus of this discussion; guidelines for this assessment exist elsewhere). Then the PoD for genomic damage is used with the exposure information to develop risk estimations (e.g., using reference dose (RfD), margin of exposure (MOE) approaches) in a risk characterization and presented to risk managers for informing decision making. This approach is applicable now for incorporating genomic damage results into the decision‐making process for assessing potential adverse outcomes in chemically exposed humans and is consistent with the ILSI HESI Risk Assessment in the 21st Century (RISK21) roadmap. This applies to any substance to which humans are exposed, including pharmaceuticals, agricultural products, food additives, and other chemicals. It is time for regulatory bodies to incorporate the broader knowledge and insights provided by genomic damage results into the assessments of risk to more fully understand the potential of adverse outcomes in chemically exposed humans, thus improving the assessment of risk due to genomic damage. The historical use of genomic damage data as a yes/no gateway for possible cancer risk has been too narrowly focused in risk assessment. The recent advances in assaying for and understanding genomic damage, including eventually epigenetic alterations, obviously add a greater wealth of information for determining potential risk to humans. Regulatory bodies need to embrace this paradigm shift from hazard identification to quantitative analysis and to incorporate the wider range of genomic damage in their assessments of risk to humans. The quantitative analyses and methodologies discussed here can be readily applied to genomic damage testing results now. Indeed, with the passage of the recent update to the Toxic Substances Control Act (TSCA) in the US, the new generation testing strategy for genomic damage described here provides a regulatory agency (here the US Environmental Protection Agency (EPA), but suitable for others) a golden opportunity to reexamine the way it addresses risk‐based genomic damage testing (including hazard identification and exposure). Environ. Mol. Mutagen. 58:264–283, 2017.
Critical Reviews in Toxicology | 2014
Matthew J. LeBaron; B. Bhaskar Gollapudi; Claire Terry; Richard Billington; Reza J. Rasoulpour
Abstract Sulfoxaflor, a novel active substance that targets sap-feeding insects, induced rodent hepatotoxicity when administered at high dietary doses. Specifically, hepatocellular adenomas and carcinomas increased after 18 months in male and female CD-1 mice at 750 and 1250 ppm, respectively, and hepatocellular adenomas increased after 2 years in male F344 rats at 500 ppm. Studies to determine the mode of action (MoA) for these liver tumors were performed in an integrated and prospective manner as part of the standard battery of toxicology studies such that the MoA data were available prior to, or by the time of, the completion of the carcinogenicity studies. Sulfoxaflor is not genotoxic and the MoA data support the following key events in the etiology of the rodent liver tumors: (1) CAR nuclear receptor activation and (2) hepatocellular proliferation. The MoA data were evaluated in a weight of evidence approach using the Bradford Hill criteria for causation and were found to align with dose and temporal concordance, biological plausibility, coherence, strength, consistency, and specificity for a CAR-mediated MoA while excluding other alternate MoAs. The available data include: activation of CAR, Cyp2b induction, hepatocellular hypertrophy and hyperplasia, absence of liver effects in KO mice, absence of proliferation in humanized mice, and exclusion of other possible mechanisms (e.g., genotoxicity, cytotoxicity, AhR, or PPAR activation), and indicate that the identified rodent liver tumor MoA for sulfoxaflor would not occur in humans. In this case, sulfoxaflor is considered not to be a potential human liver carcinogen.
Rapid Communications in Mass Spectrometry | 2011
Fagen Zhang; David L. Rick; Lynn Kan; A. W. Perala; David R. Geter; Matthew J. LeBaron; Michael J. Bartels
The possible interaction of environmental contaminants with the endocrine system has been an environmental concern since the early 1990s. To examine these interactions test guidelines have been introduced by regulatory agencies to screen for possible endocrine active compounds. One of these guidelines is the EPAs OPPTS 890.1550 [Steroidogenesis (Human Cell Line-H295R)]. This guideline requires the quantification of two major biomarkers (testosterone and estradiol) in various biological test systems. Traditional quantitation methodologies such as Radioimmunoassay (RIA) and Enzyme-linked Immunosorbent Assay (ELISA) have been used to quantify low levels of steroids. However, those methodologies have drawbacks such as the radioactive safety, antibody availability, separate assay for each biomarker, and lack of selectivity. In the current study, a rapid and sensitive liquid chromatography/positive atmospheric pressure photoionization tandem mass spectrometry method (LC/APPI-MS/MS) has been developed and validated for the simultaneous quantitation of testosterone and estradiol in the H295R cell line. Briefly, the media from cultured cells was extracted with dichloromethane (CH(2)Cl(2)) containing internal standards of both testosterone-d(3) and estradiol-(13)C(3); then, the extracted organic layer was concentrated down to dryness. The final residue was derivatized with dansyl chloride solution, and directly analyzed by LC/APPI-MS/MS. The calibration curves, with concentration ranging from 10 to 2500 pg/mL, were linear with coefficient >0.99. The lower limits of quantitation for both testosterone and estradiol were 10 pg/mL. This method was successfully validated to support requirements of the current EPA Steroidogenesis guideline. This type of method may also provide value for rapid and precise measurements of these two hormones in other in vitro or in vivo test systems.
Toxicological Sciences | 2014
Matthew J. LeBaron; Reza J. Rasoulpour; B. Bhaskar Gollapudi; Radhakrishna Sura; H. Lynn Kan; Melissa R. Schisler; Lynn H. Pottenger; Sabitha Papineni; David L. Eisenbrandt
The key events responsible for mouse liver tumors induced by a pesticide (viz., pronamide) were investigated in a series of studies employing molecular, biochemical, cellular, and apical endpoints. Based on these studies, it was demonstrated that the liver tumors were mediated by a mode of action (MoA) involving nuclear receptors (NRs) through the following key events: (1) CAR and PPAR-α receptor activation, (2) increased hepatocellular proliferation, eventually leading to (3) hepatocellular tumors. Specifically, gene expression analysis indicated robust, simultaneous coactivation of the CAR and PPAR-α NRs, as indicated by the induction of hepatic Cyp2b10 and Cyp4a10 transcripts, in response to dietary administration of pronamide to mice. The presence of hepatocellular hypertrophy and peroxisome proliferation was indicative of the activation of these two NRs at carcinogenic dose levels. Demonstrated induction of Cyp2b10 gene and protein, however, was not accompanied by enhancement of the corresponding enzyme activity (7-pentoxyresorufin-O-dealkylase (PROD)), suggesting that pronamide administration resulted in mechanism-based (suicide) inhibition of the enzyme in vivo. This was confirmed with an in vitro assay for suicide inhibition, where pronamide and/or its metabolites irreversibly inhibited Cyp2b10-mediated PROD activity. Analysis of hepatocellular proliferation via BrdU incorporation indicated a clear dose- and duration-related induction of S-phase DNA synthesis only in animals treated at and above the carcinogenic dose level. The available MoA data were evaluated for weight-of-evidence based upon the Bradford Hill criteria, followed by a human relevance framework. The conclusion from this evaluation is that pronamide-induced mouse liver tumors occur via an NR-mediated MoA involving CAR and PPAR-α activation and this MoA is not relevant to humans based on qualitative/quantitative differences between mice and humans.