Chemical Prioritization Methods for Nuclear Receptor Modulators at the U.S. EPA
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(12) United States Patent (10) Patent No.: US 9,394,315 B2 Aicher Et Al
USOO93943 15B2 (12) United States Patent (10) Patent No.: US 9,394,315 B2 Aicher et al. (45) Date of Patent: Jul.19, 2016 (54) TETRAHYDROI18NAPHTHYRIDINE 6,605,634 B2 8, 2003 Zablocki et al. SULFONAMIDE AND RELATED 6,638,960 B2 10/2003 Assmann et al. 6,683,091 B2 1/2004 Asberomet al. COMPOUNDS FOR USEAS AGONSTS OF 6,828,344 B1 12/2004 Seehra et al. RORY AND THE TREATMENT OF DISEASE 7,084, 176 B2 8, 2006 Morie et al. 7,138.401 B2 11/2006 Kasibhatla et al. (71) Applicant: Lycera Corporation, Ann Arbor, MI 7,329,675 B2 2/2008 Cox et al. 7,420,059 B2 9, 2008 O'Connor et al. (US) 7,482.342 B2 1/2009 D’Orchymont et al. 7,569,571 B2 8/2009 Dong et al. (72) Inventors: Thomas D. Aicher, Ann Arbor, MI (US); 7,696,200 B2 4/2010 Ackermann et al. Peter L. Toogood, Ann Arbor, MI (US); 7,713.996 B2 5/2010 Ackermann et al. Xiao Hu, Northville, MI (US) 7,741,495 B2 6, 2010 Liou et al. 7,799,933 B2 9/2010 Ceccarelli et al. (73) Assignee: Lycera Corporation, Ann Arbor, MI 2006,0004000 A1 1/2006 D'Orchymont et al. 2006/010O230 A1 5, 2006 Bischoff et al. (US) 2007/0010537 A1 1/2007 Hamamura et al. 2007/OO 10670 A1 1/2007 Hirata et al. (*) Notice: Subject to any disclaimer, the term of this 2007/0049556 A1 3/2007 Zhang et al. patent is extended or adjusted under 35 2007/0060567 A1 3/2007 Ackermann et al. -
OSPAR Background Document on Methoxychlor ______
Hazardous Substances Series --------------------------------------------------------------------------------------------------------------------- Methoxychlor1 OSPAR Commission 2002 (2004 Update) 1 Secretariat’s note: A review statement on methoxychlor (Publication 352d/2008) was adopted in 2008, highlighting new developments since the adoption of the Background Document. OSPAR Commission, 2002: OSPAR Background Document on Methoxychlor _______________________________________________________________________________________________________ The Convention for the Protection of the Marine Environment of the North-East Atlantic (the “OSPAR Convention”) was opened for signature at the Ministerial Meeting of the former Oslo and Paris Commissions in Paris on 22 September 1992. The Convention entered into force on 25 March 1998. It has been ratified by Belgium, Denmark, Finland, France, Germany, Iceland, Ireland, Luxembourg, Netherlands, Norway, Portugal, Sweden, Switzerland and the United Kingdom and approved by the European Community and Spain. La Convention pour la protection du milieu marin de l'Atlantique du Nord-Est, dite Convention OSPAR, a été ouverte à la signature à la réunion ministérielle des anciennes Commissions d'Oslo et de Paris, à Paris le 22 septembre 1992. La Convention est entrée en vigueur le 25 mars 1998. La Convention a été ratifiée par l'Allemagne, la Belgique, le Danemark, la Finlande, la France, l’Irlande, l’Islande, le Luxembourg, la Norvège, les Pays-Bas, le Portugal, le Royaume-Uni de Grande Bretagne et d’Irlande du Nord, la Suède et la Suisse et approuvée par la Communauté européenne et l’Espagne. © OSPAR Commission, 2002. Permission may be granted by the publishers for the report to be wholly or partly reproduced in publications provided that the source of the extract is clearly indicated. © Commission OSPAR, 2002. -
(A) Sources, Including As Appropriate (Provide Summary Information
UNEP/POPS/POPRC.1/4 Format for submitting pursuant to Article 8 of the Stockholm Convention the information specified in Annex E of the Convention Introductory information Name of the submitting Party/observer NGO Observer: Pesticide Action Network on behalf of the International POPs Elimination Network (IPEN) Contact details Clare Butler Ellis PhD, M.Inst.P, C.Env. Pesticide Action Network UK [email protected] Joseph DiGangi, PhD Environmental Health Fund +001-312-566-0985 [email protected] Chemical name Chlordecone Chemical name: 1,1a,3,3a,4,5,5,5a,5b,6-decachloro-octahydro-1,3,4-metheno-2H- cyclobuta[cd]pentalen-2-one CAS=143-50-0 Common trade names: GC 1189, Kepone, Merex Synonyms: Chlordecone, Chlordecone Kepone, Decachloroketone, Decachlorooctahydro-1,3,4-metheno-2H-cyclobuta(cd)pentalen-2-one, Decachloropentacyclo(5.3.0.0.0.0 2,6,4,10,5,9)decane-3-one, Decachlorotetracyclodecanone decachlorooctahydro- , Date of submission 27 January 2006 (a) Sources, including as appropriate (provide summary information and relevant references) (i) Production data: Quantity 1 “Chlordecone is no longer produced commercially in the United States. Between 1951 and 1975, approximately 3.6 million pounds (1.6 million kg) of chlordecone were produced in the United States (Epstein 1978). During this period, Allied Chemical Annex E information on chlordecone 1 UNEP/POPS/POPRC.1/4 Company produced approximately 1.8 million pounds (816,500 kg) of chlordecone at plants in Claymont, Delaware; Marcus Hook, Pennsylvania and Hopewell, Virginia. In 1974, because of increasing demand for chlordecone and a need to use their facility in Hopewell, Virginia, for other purposes, Allied Chemical transferred its chlordecone manufacturing to Life Sciences Products Company (EPA 1978b). -
High-Throughput H295R Steroidogenesis Assay: Utility As an Alternative and a Statistical Approach to Characterize Effects on Steroidogenesis Derik E
High-throughput H295R steroidogenesis assay: utility as an alternative and a statistical approach to characterize effects on steroidogenesis Derik E. Haggard ORISE Postdoctoral Fellow National Center for Computational Toxicology Computational Toxicology Communities of Practice Dec. 14th, 2017 The views expressed in this presentation are those of the author and do not necessarily reflect the views or policies of the U.S. EPA Outline • Background • Objectives • Assay Background • Methods and Results 1. Evaluation of the HT-H295R assay 2. Development of a quantitative prioritization metric for the HT-H295R assay data • Summary and Conclusions 2 Steroid Hormone Biosynthesis & Metabolism • Proper steroidogenesis is essential: • In utero for fetal development • In adults for reproductive function • Disruption can result in congenital adrenal hyperplasia, sterility, prenatal virilization, salt wasting, etc. • >90% of steroidogenesis occurs in the gonads • Leydig cells (males) or follicular cells (females) • Adrenal gland (corticosteroids) 3 https://www.pharmacorama.com/en/Sections/Androgen_steroid_hormones.php US EPA Endocrine Disruptor Screening Program (EDSP) • EDSP mandated to screen chemicals for endocrine activity (estrogen, androgen, thyroid) • Initial tiered screen relied on low-throughput assays • Modernization of EDSP (EDSP21) to use high-throughput and computational methods • Prioritize the universe of EDSP chemicals for endocrine bioactivity • Altering hormone levels via disruption of biosynthesis or metabolism can also contribute -
Supplemental File 11
Supplemental File 11 Supplemental Table 11. OECD Reference Chemical Performance in HT H295R versus OECD inter-laboratory results and literature-reported results. Chemical identifiers (chemical name and casn) are provided for the 25 reference chemicals that overlapped between high-throughput (HT) H295R screening and the OECD inter-laboratory validation study (Hecker et al., 2011). Trilostane, glyphosate, and human chorionic gonadotrophin were not screened in the HT H295R assay. The adjusted maxmMd value, quadrants of the steroid synthesis pathway affected (progestagens (P), glucocorticoids (G), androgens (A), and/or estrogens (E)), and the number of steroid hormones affected using the ANOVA-based logic described in the main text are also provided. The OECD inter-laboratory results for estradiol (E2) and testosterone (T) are summarized along with a brief overview of additional information from the reported literature for activity in the H295R assay (if other in vitro assay data are referenced, the assay type is provided). Only 2 of the 25 chemicals with overlapping data were reported as negative for effects on both E2 and T: ethylene dimethanesulfonate and benomyl. NA indicates that no concentration-response screening data were available (only single concentration screening available). # Chemical identifiers Results from HT H295R assay OECD Inter-laboratory and literature-reported Chemical name casn Adjusted maxmMd Quadrants # Steroid results of steroid hormones biosynthesis affected pathway affected 1 Mifepristone 84371-65-3 27 P 2 Used pharmacologically as an abortifacient with antiprogestagen, antiglucocorticoid, and antiandrogen properties. Moderate induction of E2 (2 to 4-fold induction) and T (equivocal) synthesis (Hecker, et al., 2011). Strong modulation of glucocorticoid pathway in H295R cells as a GR antagonist (Asser et al., 2014). -
Hormonal Side Effects in Patients Using Levetiracetam
Reproductive endocrine side effects of antiepileptic drugs Student Thesis Student: Marte Wendel Gustavsen Class V-03 University of Oslo, Norway Supervisor: Professor Erik Taubøll Department of Neurology, Rikshospitalet University Hospital, Oslo, Norway Contents Contents ...................................................................................................................................... 2 Acknowledgements .................................................................................................................... 3 Abstract ...................................................................................................................................... 4 Introduction ................................................................................................................................ 5 Reproductive endocrine effects of epilepsy ............................................................................... 5 Reproductive hormones can affect epilepsy ............................................................................... 7 Reproductive hormones can influence on AEDs ....................................................................... 9 Reproductive endocrine effects of AEDs ................................................................................... 9 Reproductive endocrine effects of valproate ........................................................................ 11 Women ............................................................................................................................ -
December 12, 1995. Title
AN ABSTRACT OF THE THESIS OF Sirinmas Intharapanith for the degree of Master of Science in Toxicology presented on December 12, 1995.Title:Effect of Xenoestrogen Exposure on The Expression of Cytocluome P450 Isoforms in Rainbow Trout Liver. Redacted for privacy Abstract approved: Donald R. Buhler Experimental evidence revealsthat xenoestrogens such asorganochlorine pesticides, pharmaceuticals, phenolic compounds and phytoestrogen exhibit reproductive effects on the health of human and wildlife populations. In rainbow trout, injection with 1713-estradiol represses expression of cytochrome P450s (CYP2K1, CYP2M1 and P450 LMC5) and reduces hepatic lauric acid hydroxylase activity. The aim of our study was to examine the effect on the regulation of rainbow trout P450s of four xenoestrogenic chemicals from the following categories:pesticides, pharmaceuticals, surfactants and phytoestrogens. Therefore, four chemicals, methoxychlor (20 mg/kg), diethylstilbestrol (15 mg/kg), 4-tert-octylphenol (25 and 50 mg/kg) and biochanin A (25 and 50 mg/kg) were injected (ip) on days 1,4 and 7 into one-year old juvenile rainbow trout using propylene glycol as vehicle. All fish were sacrificed on day 9.Plasma vitellogenin levels were measured by ELISA and used as an indicator of the estrogenic activity of the four chemicals. Plasma vitellogenin increased in all treated trout to varying degrees, ranging from high to low, in response to the test chemicals in the following order of decreasing of activities: diethylstilbestrol (15 mg/kg), 4-tert-octylphenol (50 mg/kg), 4-tert-octylphenol (25 mg/kg), biochanin A (50 mg/kg), biochanin A (25 mg/kg) and methoxychlor (20 mg/kg), respectively. As found upon treatment with estrogens, all four chemicals treated trout liver microsomes markedly repressed expression of P450's in liver microsomes from treated trout as measured by Western blots.Laurie acid hydroxylase activity also was greatly reduced in trout treated with all four chemicals. -
Residue Dynamics and Risk Assessment of Prochloraz and Its Metabolite 2,4,6-Trichlorophenol in Apple
Article Residue Dynamics and Risk Assessment of Prochloraz and Its Metabolite 2,4,6-Trichlorophenol in Apple Qingkui Fang 1, Gengyou Yao 2, Yanhong Shi 2, Chenchun Ding 1, Yi Wang 2, Xiangwei Wu 2, Rimao Hua 2 and Haiqun Cao 1,* 1 School of Plant Protection, Provincial Key Laboratory for Agri-Food Safety, Anhui Agricultural University, Hefei 230036, China; [email protected] (Q.F.); [email protected] (C.D.) 2 School of Resource & Environment, Provincial Key Laboratory for Agri-Food Safety, Anhui Agricultural University, Hefei 230036, China; [email protected] (G.Y.); [email protected] (Y.S.); [email protected] (Y.W.); [email protected] (X.W.); [email protected] (R.H.) * Correspondence: [email protected] Received: 22 September 2017; Accepted: 19 October 2017; Published: 20 October 2017 Abstract: The residue dynamics and risk assessment of prochloraz and its metabolite 2,4,6- trichlorophenol (2,4,6-TCP) in apple under different treatment concentrations were investigated using a GC-ECD method. The derivatization percent of prochloraz to 2,4,6-TCP was stable and complete. The recoveries of prochloraz and 2,4,6-TCP were 82.9%–114.4%, and the coefficients of variation (CV) were 0.7%–8.6% for the whole fruit, apple pulp, and apple peel samples. Under the application of 2 °C 2.0 g/L, 2 °C 1.0 g/L, 20 °C 2.0 g/L, and 20 °C 1.0 g/L treatment, the half-life for the degradation of prochloraz was 57.8–86.6 d in the whole fruit and apple peel, and the prochloraz concentration in the apple pulp increased gradually until a peak (0.72 mg·kg−1) was reached. -
A Cell-Free Testing Platform to Screen Chemicals of Potential Neurotoxic Concern Across Twenty Vertebrate Species
Environmental Toxicology and Chemistry, Vol. 36, No. 11, pp. 3081–3090, 2017 # 2017 SETAC Printed in the USA A CELL-FREE TESTING PLATFORM TO SCREEN CHEMICALS OF POTENTIAL NEUROTOXIC CONCERN ACROSS TWENTY VERTEBRATE SPECIES a,b a,b a,c,d a a,e ADELINE ARINI, KRITTIKA MITTAL, PETER DORNBOS, JESSICA HEAD, JENNIFER RUTKIEWICZ, a,b, and NILADRI BASU * aDepartment of Environmental Health Sciences, University of Michigan, Ann Arbor, Michigan, USA bFaculty of Agricultural and Environmental Sciences, McGill University, Montreal, Quebec, Canada cDepartment of Biochemistry and Molecular Biology, Michigan State University, East Lansing, Michigan, USA dInstitute for Integrative Toxicology, Michigan State University, East Lansing, Michigan, USA eToxServices, Ann Arbor, Michigan, USA (Submitted 8 February 2017; Returned for Revision 9 March 2017; Accepted 5 June 2017) Abstract: There is global demand for new in vitro testing tools for ecological risk assessment. The objective of the present study was to apply a set of cell-free neurochemical assays to screen many chemicals across many species in a relatively high-throughput manner. The platform assessed 7 receptors and enzymes that mediate neurotransmission of g-aminobutyric acid, dopamine, glutamate, and acetylcholine. Each assay was optimized to work across 20 vertebrate species (5 fish, 5 birds, 7 mammalian wildlife, 3 biomedical species including humans). We tested the screening assay platform against 80 chemicals (23 pharmaceuticals and personal care products, 20 metal[loid]s, 22 polycyclic aromatic hydrocarbons and halogenated organic compounds, 15 pesticides). In total, 10 800 species–chemical–assay combinations were tested, and significant differences were found in 4041 cases. All 7 assays were significantly affected by at least one chemical in each species tested. -
QSAR Model for Androgen Receptor Antagonism
s & H oid orm er o t n S f a l o S l c a Journal of i n e Jensen et al., J Steroids Horm Sci 2012, S:2 r n u c o e DOI: 10.4172/2157-7536.S2-006 J ISSN: 2157-7536 Steroids & Hormonal Science Research Article Open Access QSAR Model for Androgen Receptor Antagonism - Data from CHO Cell Reporter Gene Assays Gunde Egeskov Jensen*, Nikolai Georgiev Nikolov, Karin Dreisig, Anne Marie Vinggaard and Jay Russel Niemelä National Food Institute, Technical University of Denmark, Department of Toxicology and Risk Assessment, Mørkhøj Bygade 19, 2860 Søborg, Denmark Abstract For the development of QSAR models for Androgen Receptor (AR) antagonism, a training set based on reporter gene data from Chinese hamster ovary (CHO) cells was constructed. The training set is composed of data from the literature as well as new data for 51 cardiovascular drugs screened for AR antagonism in our laboratory. The data set represents a wide range of chemical structures and various functions. Twelve percent of the screened drugs were AR antagonisms; three out of six statins showed AR antagonism, two showed cytotoxicity and one was negative. The newly identified AR antagonisms are: Lovastatin, Simvastatin, Mevastatin, Amiodaron, Docosahexaenoic acid and Dilazep. A total of 874 (231 positive, 643 negative) chemicals constitute the training set for the model. The Case Ultra expert system was used to construct the QSAR model. The model was cross-validated (leave-groups-out) with a concordance of 78.4%, a specificity of 86.1% and a sensitivity of 57.9%. -
Developmental Reprogramming of Reproductive and Metabolic Dysfunction in Sheep: Native Steroids Vs
international journal of andrology ISSN 0105-6263 REVIEW ARTICLE Developmental reprogramming of reproductive and metabolic dysfunction in sheep: native steroids vs. environmental steroid receptor modulators V. Padmanabhan, H. N. Sarma, M. Savabieasfahani, T. L. Steckler and A. Veiga-Lopez Department of Pediatrics and the Reproductive Sciences Program, The University of Michigan, Ann Arbor, MI, USA Summary Keywords: The inappropriate programming of developing organ systems by exposure to bisphenol A, endocrine disrupting chemicals, excess native or environmental steroids, particularly the contamination of our foetal programming, infertility, insulin environment and our food sources with synthetic endocrine disrupting chemi- resistance, metabolic programming, cals that can interact with steroid receptors, is a major concern. Studies with methoxychlor, neuroendocrine, ovary native steroids have found that in utero exposure of sheep to excess testoster- Correspondence: one, an oestrogen precursor, results in low birth weight offspring and leads to Vasantha Padmanabhan, Room 1109, 300 N. an array of adult reproductive ⁄ metabolic deficits manifested as cycle defects, Ingalls Building, University of Michigan, Ann functional hyperandrogenism, neuroendocrine ⁄ ovarian defects, insulin resis- Arbor, MI 48109, USA. tance and hypertension. Furthermore, the severity of reproductive dysfunction E-mail: [email protected] is amplified by excess postnatal weight gain. The constellation of adult repro- ductive and metabolic dysfunction in prenatal testosterone-treated sheep is Received 18 August 2009; revised 25 October similar to features seen in women with polycystic ovary syndrome. Prenatal 2009; accepted 27 October 2009 dihydrotestosterone treatment failed to result in similar phenotype suggesting doi:10.1111/j.1365-2605.2009.01024.x that many effects of prenatal testosterone excess are likely facilitated via aroma- tization to oestradiol. -
(12) United States Patent (10) Patent No.: US 8,486,374 B2 Tamarkin Et Al
USOO8486374B2 (12) United States Patent (10) Patent No.: US 8,486,374 B2 Tamarkin et al. (45) Date of Patent: Jul. 16, 2013 (54) HYDROPHILIC, NON-AQUEOUS (56) References Cited PHARMACEUTICAL CARRIERS AND COMPOSITIONS AND USES U.S. PATENT DOCUMENTS 1,159,250 A 11/1915 Moulton 1,666,684 A 4, 1928 Carstens (75) Inventors: Dov Tamarkin, Maccabim (IL); Meir 1924,972 A 8, 1933 Beckert Eini, Ness Ziona (IL); Doron Friedman, 2,085,733. A T. 1937 Bird Karmei Yosef (IL); Alex Besonov, 2,390,921 A 12, 1945 Clark Rehovot (IL); David Schuz. Moshav 2,524,590 A 10, 1950 Boe Gimzu (IL); Tal Berman, Rishon 2,586.287 A 2/1952 Apperson 2,617,754 A 1 1/1952 Neely LeZiyyon (IL); Jorge Danziger, Rishom 2,767,712 A 10, 1956 Waterman LeZion (IL); Rita Keynan, Rehovot (IL); 2.968,628 A 1/1961 Reed Ella Zlatkis, Rehovot (IL) 3,004,894 A 10/1961 Johnson et al. 3,062,715 A 11/1962 Reese et al. 3,067,784. A 12/1962 Gorman (73) Assignee: Foamix Ltd., Rehovot (IL) 3,092.255. A 6, 1963 Hohman 3,092,555 A 6, 1963 Horn 3,141,821 A 7, 1964 Compeau (*) Notice: Subject to any disclaimer, the term of this 3,142,420 A 7/1964 Gawthrop patent is extended or adjusted under 35 3,144,386 A 8/1964 Brightenback U.S.C. 154(b) by 1180 days. 3,149,543 A 9, 1964 Naab 3,154,075 A 10, 1964 Weckesser 3,178,352 A 4, 1965 Erickson (21) Appl.