1 Draft Report of the Oecd Validation of the Rat
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Investigating Non-Targeted Screening and Accurate Quantitation of Trace Surface Water Contaminants Using High-Resolution Mass Spectrometry
Western University Scholarship@Western Electronic Thesis and Dissertation Repository 8-8-2018 3:00 PM Investigating non-targeted screening and accurate quantitation of trace surface water contaminants using high-resolution mass spectrometry Lucas M. Morrison The University of Western Ontario Supervisor Sumarah, Mark W. The University of Western Ontario Co-Supervisor Yeung, Ken K-C. The University of Western Ontario Graduate Program in Chemistry A thesis submitted in partial fulfillment of the equirr ements for the degree in Master of Science © Lucas M. Morrison 2018 Follow this and additional works at: https://ir.lib.uwo.ca/etd Part of the Analytical Chemistry Commons, and the Environmental Chemistry Commons Recommended Citation Morrison, Lucas M., "Investigating non-targeted screening and accurate quantitation of trace surface water contaminants using high-resolution mass spectrometry" (2018). Electronic Thesis and Dissertation Repository. 5612. https://ir.lib.uwo.ca/etd/5612 This Dissertation/Thesis is brought to you for free and open access by Scholarship@Western. It has been accepted for inclusion in Electronic Thesis and Dissertation Repository by an authorized administrator of Scholarship@Western. For more information, please contact [email protected]. Abstract The human impact on surface water is a growing concern and the chemical surveying of contaminants including pharmaceuticals and pesticides is currently lacking. Neonicotinoids in particular, are among the most widely used insecticides that have prompted environmental concern and require monitoring. Chemical contaminants in environmental water samples are commonly analyzed by targeted tandem mass spectrometry. However, this requires a prior knowledge of the contaminants in the area of interest. Here, surface water samples were screened by utilizing optimized data-independent acquisition (DIA) methods and the spectra were databased for future retrospective analysis. -
COMBINED LIST of Particularly Hazardous Substances
COMBINED LIST of Particularly Hazardous Substances revised 2/4/2021 IARC list 1 are Carcinogenic to humans list compiled by Hector Acuna, UCSB IARC list Group 2A Probably carcinogenic to humans IARC list Group 2B Possibly carcinogenic to humans If any of the chemicals listed below are used in your research then complete a Standard Operating Procedure (SOP) for the product as described in the Chemical Hygiene Plan. Prop 65 known to cause cancer or reproductive toxicity Material(s) not on the list does not preclude one from completing an SOP. Other extremely toxic chemicals KNOWN Carcinogens from National Toxicology Program (NTP) or other high hazards will require the development of an SOP. Red= added in 2020 or status change Reasonably Anticipated NTP EPA Haz list COMBINED LIST of Particularly Hazardous Substances CAS Source from where the material is listed. 6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9,10,10- hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide Acutely Toxic Methanimidamide, N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]- Acutely Toxic 1-(2-Chloroethyl)-3-(4-methylcyclohexyl)-1-nitrosourea (Methyl-CCNU) Prop 65 KNOWN Carcinogens NTP 1-(2-Chloroethyl)-3-cyclohexyl-1-nitrosourea (CCNU) IARC list Group 2A Reasonably Anticipated NTP 1-(2-Chloroethyl)-3-cyclohexyl-1-nitrosourea (CCNU) (Lomustine) Prop 65 1-(o-Chlorophenyl)thiourea Acutely Toxic 1,1,1,2-Tetrachloroethane IARC list Group 2B 1,1,2,2-Tetrachloroethane Prop 65 IARC list Group 2B 1,1-Dichloro-2,2-bis(p -chloropheny)ethylene (DDE) Prop 65 1,1-Dichloroethane -
OECD Environment Health and Safety Publications Series on Testing and Assessment No
OECD Environment Health and Safety Publications Series on Testing and Assessment No. 21 Detailed Review Paper Appraisal of Test Methods for Sex Hormone Disrupting Chemicals Environment Directorate ORGANISATION FOR ECONOMIC CO-OPERATION AND DEVELOPMENT Paris May 2001 1 Also Published in the Series Testing and Assessment: No. 1, Guidance Document for the Development of OECD Guidelines for Testing of Chemicals (1993; reformatted 1995) No. 2, Detailed Review Paper on Biodegradability Testing (1995) No. 3, Guidance Document for Aquatic Effects Assessment (1995) No. 4, Report of the OECD Workshop on Environmental Hazard/Risk Assessment (1995) No. 5, Report of the SETAC/OECD Workshop on Avian Toxicity Testing (1996) No. 6, Report of the Final Ring-test of the Daphnia magna Reproduction Test (1997) No. 7, Guidance Document on Direct Phototransformation of Chemicals in Water (1997) No. 8, Report of the OECD Workshop on Sharing Information about New Industrial Chemicals Assessment (1997) No. 9 Guidance Document for the Conduct of Studies of Occupational Exposure to Pesticides During Agricultural Application (1997) No. 10, Report of the OECD Workshop on Statistical Analysis of Aquatic Toxicity Data (1998) No. 11, Detailed Review Paper on Aquatic Testing Methods for Pesticides and industrial Chemicals (1998) No. 12, Detailed Review Document on Classification Systems for Germ Cell Mutagenicity in OECD Member Countries (1998) No. 13, Detailed Review Document on Classification Systems for Sensitising Substances in OECD Member Countries 1998) No. 14, Detailed Review Document on Classification Systems for Eye Irritation/Corrosion in OECD Member Countries (1998) No. 15, Detailed Review Document on Classification Systems for Reproductive Toxicity in OECD Member Countries (1998) No. -
Detection of Estrogen Receptor Endocrine Disruptor Potency of Commonly Used Organochlorine Pesticides Using the LUMI-CELL ER Bioassay
DEVELOPMENTAL AND REPRODUCTIVE TOXICITY Detection of Estrogen Receptor Endocrine Disruptor Potency of Commonly Used Organochlorine Pesticides Using The LUMI-CELL ER Bioassay John D. Gordon1, Andrew C: Chu1, Michael D. Chu2, Michael S. Denison3, George C. Clark1 1Xenobiotic Detection Systems, Inc., 1601 E. Geer St., Suite S, Durham, NC 27704, USA 2Alta Analytical Perspectives, 2714 Exchange Drive, Wilmington, NC 28405, USA 3Dept. of Environmental Toxicology, Meyer Hall, Univ. of California, Davis; Davis, CA 95616 USA Introduction Organochlorine pesticides are found in many ecosystems worldwide as result of agricultural and industrial activities and exist as complex mixtures. The use of these organochlorine pesticides has resulted in the contamination of lakes and streams, and eventually the animal and human food chain. Many of these pesticides, such as pp ’-DDT, pp ’-DDE, Kepone, Vinclozolin, and Methoxychlor (a substitute for the banned DDT), have been described as putative estrogenic endocrine disruptors, and act by mimicking endogenous estrogen 1-3 . Estrogenic compounds can have a significant detrimental effect on the endocrine and reproductive systems of both human and other animal populations 4 . Previous studies have shown a strong association between several EDCs (17p-Estradiol, DES, Zeralanol, Zeralenone, Coumestrol, Genistein, Biochanin A, Diadzein, Naringenin, Tamoxifin) and estrogenic activity via uterotropic assay, cell height, gland number, increased lactoferrin, and a transcriptional activity assay using BG1Luc4E2 cells4 . Some other examples of the effects of these EDCs are: decreased reproductive success and feminization of males in several wildlife species; increased hypospadias along with reductions in sperm counts in men; increase in the incidence of human breast and prostate cancers; and endometriosis 3-5 . -
WO 2012/148799 Al 1 November 2012 (01.11.2012) P O P C T
(12) INTERNATIONAL APPLICATION PUBLISHED UNDER THE PATENT COOPERATION TREATY (PCT) (19) World Intellectual Property Organization International Bureau (10) International Publication Number (43) International Publication Date WO 2012/148799 Al 1 November 2012 (01.11.2012) P O P C T (51) International Patent Classification: (81) Designated States (unless otherwise indicated, for every A61K 9/107 (2006.01) A61K 9/00 (2006.01) kind of national protection available): AE, AG, AL, AM, A 61 47/10 (2006.0V) AO, AT, AU, AZ, BA, BB, BG, BH, BR, BW, BY, BZ, CA, CH, CL, CN, CO, CR, CU, CZ, DE, DK, DM, DO, (21) International Application Number: DZ, EC, EE, EG, ES, FI, GB, GD, GE, GH, GM, GT, HN, PCT/US2012/034361 HR, HU, ID, IL, IN, IS, JP, KE, KG, KM, KN, KP, KR, (22) International Filing Date: KZ, LA, LC, LK, LR, LS, LT, LU, LY, MA, MD, ME, 20 April 2012 (20.04.2012) MG, MK, MN, MW, MX, MY, MZ, NA, NG, NI, NO, NZ, OM, PE, PG, PH, PL, PT, QA, RO, RS, RU, RW, SC, SD, (25) Filing Language: English SE, SG, SK, SL, SM, ST, SV, SY, TH, TJ, TM, TN, TR, (26) Publication Language: English TT, TZ, UA, UG, US, UZ, VC, VN, ZA, ZM, ZW. (30) Priority Data: (84) Designated States (unless otherwise indicated, for every 61/480,259 28 April 201 1 (28.04.201 1) US kind of regional protection available): ARIPO (BW, GH, GM, KE, LR, LS, MW, MZ, NA, RW, SD, SL, SZ, TZ, (71) Applicant (for all designated States except US): BOARD UG, ZM, ZW), Eurasian (AM, AZ, BY, KG, KZ, MD, RU, OF REGENTS, THE UNIVERSITY OF TEXAS SYS¬ TJ, TM), European (AL, AT, BE, BG, CH, CY, CZ, DE, TEM [US/US]; 201 West 7th St., Austin, TX 78701 (US). -
Prenatal Testosterone Supplementation Alters Puberty Onset, Aggressive Behavior, and Partner Preference in Adult Male Rats
J Physiol Sci (2012) 62:123–131 DOI 10.1007/s12576-011-0190-7 ORIGINAL PAPER Prenatal testosterone supplementation alters puberty onset, aggressive behavior, and partner preference in adult male rats Cynthia Dela Cruz • Oduvaldo C. M. Pereira Received: 26 October 2011 / Accepted: 19 December 2011 / Published online: 11 January 2012 Ó The Physiological Society of Japan and Springer 2012 Abstract The objective of this study was to investigate because pregnant women exposed to hyperandrogenemia whether prenatal exposure to testosterone (T) could change and then potentially exposing their unborn children to ele- the body weight (BW), anogenital distance (AGD), ano- vated androgen levels in the uterus can undergo alteration of genital distance index (AGDI), puberty onset, social normal levels of T during the sexual differentiation period, behavior, fertility, sexual behavior, sexual preference, and T and, as a consequence, affect the reproductive and behavior level of male rats in adulthood. To test this hypothesis, patterns of their children in adulthood. pregnant rats received either 1 mg/animal of T propionate diluted in 0.1 ml peanut oil or 0.1 ml peanut oil, as control, Keywords Aggressive behavior Á Male rats Á on the 17th, 18th and 19th gestational days. No alterations in Prenatal testosterone Á Puberty onset Á Sexual behavior Á BW, AGD, AGDI, fertility, and sexual behavior were Sexual differentiation observed (p [ 0.05). Delayed onset of puberty (p \ 0.0001), increased aggressive behavior (p [ 0.05), altered pattern of sexual preference (p \ 0.05), and reduced T plasma level Introduction (p \ 0.05) were observed for adult male rats exposed pre- natally to T. -
The “Notice”) Is Provided to You Pursuant to and in Compliance with California Health and Safety Code Section 25249.7(D)
NOTICE OF VIOLATION California Safe Drinking Water and Toxic Enforcement Act January 17, 2020 This Notice of Violation (the “Notice”) is provided to you pursuant to and in compliance with California Health and Safety Code Section 25249.7(d). • For general information regarding the California Safe Drinking Water and Toxic Enforcement Act (“Proposition 65”), please see the attached summary prepared by California's Office of Environmental Health Hazard Assessment. • This Notice is provided by Maria Elizabeth Romero, a concerned citizen of the State of California and resident of Monterey County. Description of Violation: • Violators: LGC Standards Inc. LGC North America, Inc. VHG Labs, Incorporated LGC Limited (collectively, “LGC”) • Time Period of Exposure: The violations have been occurring since at latest January 17, 2018, and are ongoing. • Statutory Authority: This Notice is provided for failure to comply with the warning requirements of Proposition 65, found at California Health and Safety Code section 25249.6. • Chemicals Involved: The chemicals involved in these violations are listed in Attachment B hereto, and have been identified by the State of California as causing cancer or reproductive harm. • Type of Product: All products offered for sale by LGC on the Web site at https://us.lgcstandards.com whose primary component is a chemical listed on Attachment B (“Covered Products”). • Description of Exposure: Student use of the Covered Products in academic laboratories results in human exposure to toxic chemicals via dermal contact, eye contact, ingestion, inhalation, and accidental injection. No clear and reasonable warning of toxicity is provided by LGC in connection with the Covered Products. / / Notice of Violation Romero / LGC Page 2 Resolution of Noticed Claim: Within the next 60 days, California's Office of the Attorney General and other government attorneys may choose to bring an enforcement action against you in this matter. -
California Proposition 65 (Prop65)
20 NOVEMBER 2018 To Whom It May Concern: Certificate of Compliance California Proposition 65 California’s Proposition 65 entitles California consumers to special warnings for products that contain chemicals known to the state of California to cause cancer and birth defects or other reproductive harm if those products expose consumers to such chemicals above certain threshold levels. This is to certify that Alliance Memory comply with Safe Drinking Water and Toxic Enforcement Act of 1986, commonly known as California Proposition 65, that are ‘known to the state to cause cancer or reproductive toxicity’ as of December 29, 2017, by following the labelling guidelines set out therein. Alliance Memory labelling system clearly states a ‘Prop65 warning’ as and when necessary, on product packaging that is destined for the state of California, USA. This document certifies that to the best of our current knowledge and belief and under normal usage, Alliance Memory’s IC products are in compliance with California Proposition 65 – The Safe Drinking Water and Toxic Enforcement Act, 1986) and do not contain chemical elements of those listed within the California Proposition 65 chemical listing as shown below. Signature : Date: 20 November 2018 Name : Kim Bagby Title : Director QRA Department/Alliance Memory California Proposition 65 list of chemicals. The following is a list of chemicals published as a requirement of Safe Drinking Water and Toxic Enforcement Act of 1986, commonly known as California Proposition 65, that are ‘known to the state to cause -
Health Effects Support Document for 1,1-Dichloro-2,2- Bis(P-Chlorophenyl)Ethylene (DDE)
Health Effects Support Document for 1,1-Dichloro-2,2- bis(p-chlorophenyl)ethylene (DDE) Health Effects Support Document for 1,1-Dichloro-2,2-bis(p-chlorophenyl)ethylene (DDE) U.S. Environmental Protection Agency Office of Water (4304T) Health and Ecological Criteria Division Washington, DC 20460 www.epa.gov/safewater/ccl/pdf/DDE.pdf EPA Document Number EPA-822-R-08-003 January, 2008 Printed on Recycled Paper DDE — January, 2008 iv FOREWORD The Safe Drinking Water Act (SDWA), as amended in 1996, requires the Administrator of the Environmental Protection Agency (EPA) to establish a list of contaminants to aid the Agency in regulatory priority setting for the drinking water program. In addition, the SDWA requires EPA to make regulatory determinations for no fewer than five contaminants by August 2001 and every five years thereafter. The criteria used to determine whether or not to regulate a chemical on the Contaminant Candidate List (CCL) are the following: • The contaminant may have an adverse effect on the health of persons. • The contaminant is known to occur or there is a substantial likelihood that the contaminant will occur in public water systems with a frequency and at levels of public health concern. • In the sole judgment of the Administrator, regulation of such contaminant presents a meaningful opportunity for health risk reduction for persons served by public water systems. The Agency’s findings for all three criteria are used in making a determination to regulate a contaminant. The Agency may determine that there is no need for regulation when a contaminant fails to meet one of the criteria. -
Report on Pesticide Rapid Assessments
REPORT ON PESTICIDE RAPID ASSESSMENTS Minnesota Department of Health This report was prepared by the Minnesota Department of Health (MDH), Drinking Water Contaminants of Emerging Concern Program; Dan Balluff, Alexandra Barber, Jim Jacobus, Sarah Johnson, and Pam Shubat. The Pesticide Rapid Assessment Project was made possible by funds from the Clean Water Fund, from the Clean Water, Land and Legacy Amendment. For more information: Drinking Water Contaminants of Emerging Concern Program Phone: 651-201-4899 Website: www.health.state.mn.us/cec Email: [email protected] December 2014 Table of Contents Executive Summary 4 Background 5 Methods for Conducting Rapid Assessments 6 Results 10 Discussion 13 Table 1: Pesticides listed by MDA for which current assessments were available or are pending 16 Table 2: Pesticide degradates for which MDH recommends the non-cancer rapid assessment of a surrogate chemical 17 References 18 Appendix A: Rapid Assessments Table 20 Executive Summary The Minnesota Department of Health (MDH) Health Risk Assessment Unit developed a new, rapid way to assess health risks of chemicals in drinking water. Rapid assessments were completed for 159 pesticides selected by the Minnesota Department of Agriculture or Minnesota Department of Health. The chemicals were selected because no MDH drinking water guidance was available or the guidance was outdated. The result of a rapid assessment is an amount of chemical in water that is unlikely to harm people who drink the water. MDH used information on toxic (harmful) effects of pesticides and risk assessment methods used by MDH for other types of drinking water guidance. The values that result from the rapid assessments are likely to be low compared to the result MDH would produce from an in-depth and lengthy review of the same chemical. -
Progestagens for Human Use. Exposure and Hazard Assessment for the Aquatic Environment J.P
Progestagens for human use. Exposure and hazard assessment for the aquatic environment J.P. Besse, J. Garric To cite this version: J.P. Besse, J. Garric. Progestagens for human use. Exposure and hazard assessment for the aquatic environment. Environmental Pollution, Elsevier, 2009, 157 (12), p. 3485 - p. 3494. 10.1016/j.envpol.2009.06.012. hal-00455636 HAL Id: hal-00455636 https://hal.archives-ouvertes.fr/hal-00455636 Submitted on 10 Feb 2010 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Environmental Pollution, vol. 157, n° 12, doi : 10.1016/j.envpol.2009.06.012 1 Progestagens for human use, exposure and hazard assessment for 2 the aquatic environment 3 4 5 6 Reviewed version of manuscript ENVPOL-D-09-00080R1. 7 The abstract of this paper was evaluated and approved by Dr Wiegand. 8 9 10 Authors 11 12 Jean-Philippe BESSE a* 13 Jeanne GARRIC a** 14 15 a Unité Biologie des écosystèmes aquatiques. Laboratoire d’écotoxicologie, 16 Cemagref, 3bis quai Chauveau CP 220 69336 Lyon cedex 09, France 17 Tel.: +33 472208902 18 19 * first author 20 ** corresponding author. E-mail address: [email protected] 21 22 23 Capsule: 24 Gestagens exposure and hazard assessment for the aquatic environment. -
Pesticides in Streams in New Jersey and Long Island, New
PESTICIDES IN STREAMS IN NEW JERSEY National Water-Quality AND LONG ISLAND, NEW YORK, AND Assessment Program Long Island - New Jersey RELATION TO LAND USE Study Unit Abstract Pesticide compounds were detected in all 50 water samples collected from streams in New Jersey and Long Island, New York, during June 9-18, 1997. Samples were analyzed for 47 compounds, of which 25 were detected. The number of pesticides detected at each site ranged from 1 to 14. The seven most frequently detected pesticides were atrazine (in 93 percent of samples), metolachlor (86 percent), prometon (84 percent), desethyl-atrazine (78 percent), simazine (78 percent), carbaryl (44 percent), and diazinon (44 percent). All pesticide concentrations were within both U.S. Environmental Protection Agency (USEPA) and State maximum contami- nant levels (MCL’s) for drinking water and USEPA lifetime health advisory levels (HAL’s). Concentrations of dieldrin and methyl- azinphos at one or more sites, however, equaled or exceeded a Federal or State water-quality criterion for aquatic life. The pesticides detected in a stream were related to the land-use composition of the basin. Detection frequencies of 14 of the 25 pesticides detected were highest at agricultural sites; acetochlor, azinphos-methyl, carbofuran, and pebulate were detected only at agricultural sites. Seven compounds were detected most frequently at urban sites; trifluralin, dieldrin, napropamide, and benfluralin were detected only at urban sites. Four compounds were detected most frequently at sites draining areas of mixed land use. No pesticides were detected most frequently at sites draining forested areas. The median concentration and the detection frequency of a given pesticide always were highest in samples from sites in the same land-use category.The median concentrations of seven pesticides at the agricultural sites were at least twice as high as the median concentrations at sites in other land-use categories.