DNA Methylation in Rat Liver by Daminozide, 1, 1-Dimethylhydrazine, and Dirnethylnitrosamine

Total Page:16

File Type:pdf, Size:1020Kb

DNA Methylation in Rat Liver by Daminozide, 1, 1-Dimethylhydrazine, and Dirnethylnitrosamine f1.JNDAMENTAL AND APPLIED TOXICOLOGY 11, 723-7 30 ( 1988)' DNA Methylation in Rat Liver by Daminozide, 1, 1-Dimethylhydrazine, and Dirnethylnitrosamine PETER SAGELSDORFF, WERNER K. LUTZ, 1 AND CHRISTIAN SCHLATTER Institute ofToxicology, Swiss Federal Institute ofTechnology and University ofZürich, CH-8603 Schwerzenbach, Switzerland Received February8, 1988: accepted May 27, 1988 DNA Methylation in Rat Li ver by Daminozide, 1, 1-Dimethylhydrazine, and Dimethylnitros­ amine. SAGELSDORFF, P., LUTZ, W. K., AND ScHLAITER C. (1988). Fundam. Appl. Toxico/. 11, 723-730. [methyP4C]Daminozide (succinic acid 2',2'-dimethylhydrazide; 37 mgjkg), l,l­ (14C]dimethylhydrazine (UDMH; 19 mgtkg), and (14C]dimethylnitrosamine (DMNA; 0.1 mg/ kg) were administered by oral gavage to male Sprague-Dawley rats. After 24 hr, the animals were killed and DNA was purified from the livers to constant specific radioactivity. After enzymatic degradation of the DNA to the 3'-deoxynucleotides the Ievel of DNA methylation was deter­ mined by HPLC analysis. Radiolabeled 7-methylguanine (7mG) was identified by cochromatog­ raphy with unlabeled 7mG added as standard after acidic depurination of DNA and HPLC analysis ofpurines and apurinic acid. All three compounds were found to methylate DNA. The relative potencies were 1:47:4900 for daminozide:UDMH:DMNA. With [methyPH]UDMH, the formation of7mG was investigated as a function of dose administered, at 20, 2, and 0.2 mgj kg. The methylation ofDNA was strictly proportional to the dose. The data were used to com­ pare the Ievel of DNA alkylation derived from residues of daminozide and UDMH in treated apple with the genotoxicity of the intake of N-nitroso compounds in Germany and Japan. It is estimated that these residues could Iead to a DNA methylation in the Iiver of about 6% of an average exposure to DMNA. © 1988 Society ofToxicology. Daminozide (succinic acid 2'-2'-dimethylhy­ tumors of the lungs, kidneys, and, for drazide; trade name of formulation: Alar) is UDMH only, the liver. The studies are a plant growth regulator used in fruit and difficult to evaluate properly, however, be­ flower culture. Degradation of the parent cause of the high toxicity of the treatments compound in the fruits as weil as in mam­ (23 and 8% survival at 70 weeks). Since dami­ mals may, under certain conditions, yield nozide was much less potent than UDMH 1, 1-dimethylhydrazine (unsymmetrical di­ (by a factor of about 200}, it is possible that methylhydrazine, UDMH). The tumorigenic UDMH formed as a metabolite might be re­ potential ofvarious substituted hydrazine de­ sponsible for the effects induced by damino­ rivatives has been investigated, almost exclu­ zide. In rats, UDMH was a very weak liver sively in one laboratory. Both daminozide carcinogen, producing tumors only late in (2% in drinking water; Toth et al., 1977) and life. It was at least two orders of magnitude UDMH (0.01% in drinking water; Toth, less potent than dimethylnitrosamine 1973) have been reported to induce angiosar­ (DMNA) (Druckrey et al., 1967). comas in mice in various organs, as weil as The putative mechanism of a tumor induc­ tion by UDMH might involve DNA methyl­ ation, in analogy to the mode of action of 1 To whom correspondence should be addressed. the potent carcinogen 1,2-dimethylhydrazine 723 0272-0590/88 $3.00 Copyright© 1988 by the Society ofToxicology. All rights of reproduction in any fonn reserved. 724 SAGELSDORFF, LUTZ, AND SCHLATTER (symmetrical dimethylhydrazine, SDMH) in [methy/-'4C]UDMH at a limit ofdetection of0.006% 14 (Lewis and Swenberg, 1983). Oxidative de­ [methyi- C]DMNA. The initial radiochemical purity of (methyl-3H]VDMH (10 Ci/mmol) was 76%. This com­ methylation ofUDMH can, in principle, Iead pound was purified before use by HPLC on a Partisil 10 to the same metabolic intermediates, so that SCX (250 X 4 mm) column followed by a Partisil5 ODS a methylation ofDNA by UDMH cannot be 3 (250 X 4 mm) column (Whatman, NJ). eluting at a flow excluded. of 1.5 ml/min with a linear gradient over 20 min from 5 The data obtained from in vitro tests on the mM HCOOH/NH3 , pH 3.6, to 300 mM HCOOH/NH3 , 50% methanol~ pH 3.6. The retention times were 9 and genotoxicity of alkylhydrazines do not corre­ 28 min for DMNA and UDMH, respectively. The frac­ late with carcinogenicity (Kier et al., 1986), tions containing UDMH were pooled and lyophilized. probably because the activation to the ulti­ The radiochemical purity of the purified [methyPH]­ mate electrophiles does not proceed quantita­ VDMH was 97.7% and contained less than 0.05% 3 tively. It was therefore the aim ofthis study [ methyl- H]DMNA. Anima/s. Male Sprague-Dawley rats [Iva:SIV-50.SD] to measure the methylating potency of dami­ were obtained at weights of about 150 g from Ivanovas, nozide and UDMH in vivo. Using the Kissleg, FRG. They were held four per macrolone cage methyl-radiolabeled compounds, it was on sawdust for 1 week for accJimatization. They were fed tested to what extent daminozide and Haltungsdiät ''A" No. 343, Klingental Mühle AG. Kais­ UDMH methylate liver DNA in male eraugst, Switzerland a'd libttum and had free access to tap water. Sprague-Dawley rats after oral administra­ Treatments. The rats received the labeled test com­ tion. The results were used to estimate the pounds in about 1 ml 0.01 N HCI by oral gavage. [methy/- Ievel of DNA methylation induced by resi­ 3H]UDMH was diluted with unlabeled UDMH (Huka dues of daminozide and UDMH in fruits, AG, Buchs, Switzerland) to the appropriate doses. The and the DNA alkylation was compared with precise dose given to each individual animal was deter­ that arising from an average intake of dimeth­ mined on the basis ofthe weight difference ofthe syringe before and after oral gavage. The values are listed in the ylnitrosamine (DMNA) with foods (Preuss­ tables. Animals receiving the 14C Iabel were placed in mann and Eisenbrand, 1984). glass metabolism cages and the exhaled air was trapped with ethanolaminejmethanol ( 1 + 4 vol) to collect ex­ pired 14C02. MATERIALS AND METHODS Iso/ation ofchromatin. Twenty-four hours after the ad­ ministration, the animals were k.illed by open heart punc­ Test compounds. The radiolabeled test compounds ture under ether anesthesia. The livers were excised and daminozide, UDMH, and DMNA were obtained from homogenized in a Teflon Potter-Elvehjem-type homog­ Chemsyn Science Labs., Lenexa. Kansas. The radio­ enizer at 4°C. Chromatin was prepared according to Sa­ chemical purity of [methy/-14C]daminozide (20.35 mCi/ gelsdorff et a/. ( 1983), essentially by precipitation with mmol) was 97 .3%, as determined by HPLC on a Lichro­ the nonionic detergent Nonidet-P40 (BDH Chemieals Ltd., Poole BH 12 4NN, England). This pellet, containing sorb RP18 (7 ~m) column (4 X 250 mm), eluting at a · ßow of 1.5 ml/min wjth 65 parts MeOH and 35 parts about 2-3 mg DNA and 20-30 mg protein per gram 0.1% (w/v) aqueous SDS solution containing 0.1% (v/v) Ii ver, was washed until the suspension contained < 1 #'Ci formic acid. Fractions of 1 min were collected and total radioactivity in order to remove the majority of counted for radioactivity after the addition of 10 ml In­ noncovalently bound radioactivity. sta-Ge) (Packard). The retention time for daminozide Isolation ojDNA. These steps were perfonned accord­ was 6 min. The radiochemical purities of [methy!-' 4C]­ ingtoSagelsdorff et al. (1983). Essentially, thechromatin UDMH (17.3 mCi/mmol), [methyl- 14C]DMNA (17.3 pellet was homogenized in a Waring biender in 25 m1 mCi/mmol), and [methyl-3H]DMNA (10.8 Cijmmol) lysing medium (1% (w/v) SOS, 10 mM EDTA, 8 M urea were determined by HPLC on a Lichrosorb RP 18 (7 ~m) in 0.24 M sodium phosphate, pH 6.8). Protein was ex­ column (4 X 250 mm) eluting at a flow of 1.5 mlfmin, tracted from the homogenate with chloroform/isoamy1 with a linear gradient over 15 min of 10-50% methanol alcohol/pheno) (CIP), phenolwas removed with diethyl­ in 50 mM sodium phosphate buffer, pH 3.5, containing ether, and the DNA was purified by adsorption on a hy­ I 0 mM octanesulfonic acid. The retention times were droxylapatite column, dialysis, and precipitation with 3 and 9 min for DMNA and UDMH, respectively. The ethanol. The highly purified DNA (mostly double radiochemical purities were 99.8, 95.9, and 90% stranded, less than 0.2% protein, as shown with radiola­ for [methy/- 14C]UDMH, [methyl- 14C), and [methyl- beled amino acid incorporation [Caviezel et al.. 1984]) 3H]DMNA; no DMNA contamination could be detected was dissolved in a 20 mM sodium succinate buffer, con- DAMINOZIDE DNA METHYLATION 725 taining 8 mM CaCh, pH 6.0. The amount of DNA was dioactivity was determined by analyzing an inactive determined by assuming an absorbance of 20 at 260 nm DNA digest. The standard deviation for each fraction for a solution of 1 mg DNA/ml. Scintillation counting was determined on the basis of 17 nucleotide anaiyses of (Packard scintillation counter Tricarb 460 CD} was per­ control DNA hydrolysates. The standard deviation of a formed on an aliquot ofthe DNA solution after addition sample containing little radioactivity was assumed to be of I 0 ml lnsta-Gel. equal to the standard deviation of the background sam­ Repetitive purification of DNA. The remaining DNA ples. The Iimit of detection for radioactivity in a fraction solutionwas mixed with 25 mllysing medium, extracted was then calculated on the basis of2 SD. twice with CIP and ether, and dialyzed and precipitated Analysis of DNA purines. DNA (0.1-1 mg) in 1.5 ml with ethanol.
Recommended publications
  • Report of the Advisory Group to Recommend Priorities for the IARC Monographs During 2020–2024
    IARC Monographs on the Identification of Carcinogenic Hazards to Humans Report of the Advisory Group to Recommend Priorities for the IARC Monographs during 2020–2024 Report of the Advisory Group to Recommend Priorities for the IARC Monographs during 2020–2024 CONTENTS Introduction ................................................................................................................................... 1 Acetaldehyde (CAS No. 75-07-0) ................................................................................................. 3 Acrolein (CAS No. 107-02-8) ....................................................................................................... 4 Acrylamide (CAS No. 79-06-1) .................................................................................................... 5 Acrylonitrile (CAS No. 107-13-1) ................................................................................................ 6 Aflatoxins (CAS No. 1402-68-2) .................................................................................................. 8 Air pollutants and underlying mechanisms for breast cancer ....................................................... 9 Airborne gram-negative bacterial endotoxins ............................................................................. 10 Alachlor (chloroacetanilide herbicide) (CAS No. 15972-60-8) .................................................. 10 Aluminium (CAS No. 7429-90-5) .............................................................................................. 11
    [Show full text]
  • California Proposition 65 Toxicity List
    STATE OF CALIFORNIA ENVIRONMENTAL PROTECTION AGENCY OFFICE OF ENVIRONMENTAL HEALTH HAZARD ASSESSMENT SAFE DRINKING WATER AND TOXIC ENFORCEMENT ACT OF 1986 CHEMICALS KNOWN TO THE STATE TO CAUSE CANCER OR REPRODUCTIVE TOXICITY 4-Mar-05 The Safe Drinking Water and Toxic Enforcement Act of 1986 requires that the Governor revise and Chemical Type of Toxicity CAS No. Date Listed A-alpha-C (2-Amino-9H-pyrido[2,3-b]indole) cancer 26148685 1-Jan-90 Acetaldehyde cancer 75070 1-Apr-88 Acetamide cancer 60355 1-Jan-90 Acetazolamide developmental 59665 20-Aug-99 Acetochlor cancer 34256821 1-Jan-89 Acetohydroxamic acid developmental 546883 1-Apr-90 2-Acetylaminofluorene cancer 53963 1-Jul-87 Acifluorfen cancer 62476599 1-Jan-90 Acrylamide cancer 79061 1-Jan-90 Acrylonitrile cancer 107131 1-Jul-87 Actinomycin D cancer 50760 1-Oct-89 Actinomycin D developmental 50760 1-Oct-92 Adriamycin (Doxorubicin hydrochloride) cancer 23214928 1-Jul-87 AF-2;[2-(2-furyl)-3-(5-nitro-2-furyl)]acrylamide cancer 3688537 1-Jul-87 Aflatoxins cancer --- 1-Jan-88 Alachlor cancer 15972608 1-Jan-89 Alcoholic beverages, when associated with alcohol abuse cancer --- 1-Jul-88 Aldrin cancer 309002 1-Jul-88 All-trans retinoic acid developmental 302794 1-Jan-89 Allyl chloride Delisted October 29, 1999 cancer 107051 1-Jan-90 Alprazolam developmental 28981977 1-Jul-90 Altretamine developmental, male 645056 20-Aug-99 Amantadine hydrochloride developmental 665667 27-Feb-01 Amikacin sulfate developmental 39831555 1-Jul-90 2-Aminoanthraquinone cancer 117793 1-Oct-89 p -Aminoazobenzene cancer
    [Show full text]
  • Alar Five Years Later
    Alar Five Years Later by Kenneth Smith This special report was written for the American Council on Science and Health by Kenneth Smith, Editorial Writer of The Washington Times as a follow-up to the two previous reports: Alar One Year Later andAlar Three Years Later. ACSH gratefully acknowledges the comments and contributions of the following individuals who reviewed one or more editions of this report: F. J. Francis, Ph.D. University of Massachusetts Lois S. Gold, Ph.D. University of California, Berkeley Thomas H. Jukes, Ph.D. University of California, Berkeley Roger P. Maickel, Ph.D. Purdue University A. Alan Moghissi, Ph.D. Temple University Robert E. Olson, M.D., Ph.D. SUNY at Stony Brook Thomas W. Orme, Ph.D. American Council on Science and Health Edward G. Remmers, Sc.D. American Council on Science and Health Joseph Rosen, Ph.D. Rutgers University Fredrick J. Stare, M.D., Ph.D. Harvard School of Public Health Elizabeth M. Whelan, Sc.D., M.P.H. American Council on Science and Health “As a pediatric surgeon, as well as the nation’s former surgeon general, I care deeply about the health of children — and if Alar ever posed a health hazard, I would have said so then and would say so now. When used in the regulated, approved manner as Alar was before it was with- drawn in 1989, Alar-treated apple products posed no hazard to the health of children or adults.” — C. Everett Koop, M.D. Executive Summary In early 1989, this country suffered the public relations equivalent of a natural disaster, one that most scientists now believe should never have occurred.
    [Show full text]
  • (12) United States Patent (10) Patent No.: US 6,586,617 B1 Tabuchi Et Al
    USOO65866.17B1 (12) United States Patent (10) Patent No.: US 6,586,617 B1 Tabuchi et al. (45) Date of Patent: Jul. 1, 2003 (54) SULFONAMIDE DERIVATIVES JP 63-307851 12/1988 JP 1-156952 6/1989 (75) Inventors: Takanori Tabuchi, Tsukuba (JP); WO 96/36596 11/1996 WO 97/24135 7/1997 Tetsuhiro Yamamoto, Toride (JP); WO 97/31910 9/1997 Masaharu Nakayama, Tsukuba (JP) WO 98/45.255 10/1998 (73) Assignee: Sumitomo Chemical Takeda Agro WO 99/06037 2/1999 Company, Limited, Tokyo (JP) WO OO/50391 8/2000 OTHER PUBLICATIONS (*) Notice: Subject to any disclaimer, the term of this patent is extended or adjusted under 35 Derek R. Buckle et al., “Inhibition of Cyclic Nucleotide U.S.C. 154(b) by 0 days. Phosphodiesterase by Derivatives of 1,3-Bis(cyclopropyl methyl)xanthine”, J. Med. Chem., vol. 37, No. 4, pp. (21) Appl. No.: 09/958,953 476-485, 1994. (22) PCT Filed: Apr. 17, 2000 Francisca Lopes et al., “Acyloxymethyl as a Drug Protecting Group. Part 6: N-Acyloxymethyl- and N-Aminocarbony (86) PCT No.: PCT/JP00/02764 loxy)methylsulfonamides as Prodrugs of Agents Contain S371 (c)(1), ing a Secondary Sulfonamide Group”, Bioorganic & (2), (4) Date: Dec. 18, 2001 Medicinal Chemistry, vol. 8, No. 4, pp. 707-716, 2000. J.S. Sukla et al., “Studies on Some Newer Possible Biologi (87) PCT Pub. No.: WO00/65913 cally Active Agents: Part II. Synthesis of N-(-aminopropyl)-2-heterocyclic-p-arylidene aminoben PCT Pub. Date: Nov. 9, 2000 ZeneSulphonamides and N(-aminopropyl)-2-heterocyclic (30) Foreign Application Priority Data Sulphanalamides and their Antibacterial Activity, J.
    [Show full text]
  • Toxicological Profile for Hydrazines. US Department Of
    TOXICOLOGICAL PROFILE FOR HYDRAZINES U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry September 1997 HYDRAZINES ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. HYDRAZINES iii UPDATE STATEMENT Toxicological profiles are revised and republished as necessary, but no less than once every three years. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology/Toxicology Information Branch 1600 Clifton Road NE, E-29 Atlanta, Georgia 30333 HYDRAZINES vii CONTRIBUTORS CHEMICAL MANAGER(S)/AUTHOR(S): Gangadhar Choudhary, Ph.D. ATSDR, Division of Toxicology, Atlanta, GA Hugh IIansen, Ph.D. ATSDR, Division of Toxicology, Atlanta, GA Steve Donkin, Ph.D. Sciences International, Inc., Alexandria, VA Mr. Christopher Kirman Life Systems, Inc., Cleveland, OH THE PROFILE HAS UNDERGONE THE FOLLOWING ATSDR INTERNAL REVIEWS: 1 . Green Border Review. Green Border review assures the consistency with ATSDR policy. 2 . Health Effects Review. The Health Effects Review Committee examines the health effects chapter of each profile for consistency and accuracy in interpreting health effects and classifying end points. 3. Minimal Risk Level Review. The Minimal Risk Level Workgroup considers issues relevant to substance-specific minimal risk levels (MRLs), reviews the health effects database of each profile, and makes recommendations for derivation of MRLs. HYDRAZINES ix PEER REVIEW A peer review panel was assembled for hydrazines. The panel consisted of the following members: 1. Dr.
    [Show full text]
  • Assays and Inhibitors for Jumonjic Domain-Containing Histone Demethylases As Epigenetic Regulators
    Assays and Inhibitors for JumonjiC Domain-Containing Histone Demethylases as Epigenetic Regulators Martin Roatsch Assays and Inhibitors for JumonjiC Domain-Containing Histone Demethylases as Epigenetic Regulators Inauguraldissertation zur Erlangung des akademischen Grades eines Doctor rerum naturalium (Dr. rer. nat.) der Fakult¨atf¨urChemie und Pharmazie der Albert-Ludwigs-Universit¨atFreiburg vorgelegt von Martin Roatsch geboren in Berlin, Deutschland 2016 Eidesstattliche Versicherung gem¨aß x7, Absatz 1, Satz 3, Nr. 8 der Promotionsordnung der Albert-Ludwigs-Universit¨atf¨urdie Fakult¨atf¨urChemie und Pharmazie 1. Bei der eingereichten Dissertation zu dem Thema Assays and Inhibitors for JumonjiC Domain-Containing Histone Demethylases as Epigenetic " Regulators\ handelt es sich um meine eigenst¨andigerbrachte Leistung. 2. Ich habe nur die angegebenen Quellen und Hilfsmittel benutzt und mich keiner unzul¨assigen Hilfe Dritter bedient. Insbesondere habe ich w¨ortlich oder sinngem¨aßaus anderen Werken ¨ubernommene Inhalte als solche kenntlich gemacht. 3. Die Dissertation oder Teile davon habe ich bislang nicht an einer Hochschule des In- oder Auslands als Bestandteil einer Pr¨ufungs-oder Qualifikationsleistung vorgelegt. 4. Die Richtigkeit der vorstehenden Erkl¨arungen best¨atigeich. 5. Die Bedeutung der eidesstattlichen Versicherung und die strafrechtlichen Folgen einer unrichtigen oder unvollst¨andigeneidesstattlichen Versicherung sind mir bekannt. Ich versichere an Eides statt, dass ich nach bestem Wissen die reine Wahrheit erkl¨artund nichts ver- schwiegen habe. Freiburg i. Br., 2. Juni 2016 Unterschrift Dekan der Fakult¨at: Prof. Dr. Manfred Jung Vorsitzender des Promotionsausschusses: Prof. Dr. Stefan Weber Referent: Prof. Dr. Manfred Jung Koreferent: Prof. Dr. Bernhard Breit Datum der m¨undlichen Pr¨ufung: 29. Juni 2016 Datum der Verpflichtung: 7.
    [Show full text]
  • Hazardous Materials List
    Hazardous Materials List Version: 1.12.2016 v 1.4 All agrochemicals, especially pesticides, can be potentially hazardous in some form or other to human and animal health as well as to the environment and therefore should be used only under caution. Fairtrade International recommends the use of other methods like proper choice of crops and varieties, suitable cultivation practices and biological material for pest, before a chemical pesticide is used for pest control. The Hazardous Materials List (HML) is divided in three lists: the Red List, the Orange List and the Yellow List. Red List: The Red List is a ‘prohibited’ list and includes materials that must not be used on Fairtrade products. Orange List: The Orange List is a ‘restricted’ List and includes materials that may be used under conditions specified in this document thus restricting their use. The use of materials in this list will be monitored by Fairtrade International. Operators should be aware that some of these materials are to be phased out by 30 June 2020 or by 30 June 2022 as indicated in the list. The other materials in the list may eventually be prohibited and are encouraged to abandon their use. Yellow List: The Yellow List is a ‘flagged’ list and includes materials which are flagged for being hazardous and should be used under extreme caution. Fairtrade International will be monitoring the classification of these materials by international bodies like PAN, WHO and FAO, and materials may be prohibited in the future. Operators are encouraged to abandon their use. Classification of materials in the HML The Hazardous Materials List includes materials that are identified as Highly Hazardous as defined in the Code of Conduct on Pesticide Management adopted by FAO and WHO in 2013.
    [Show full text]
  • Role of Chlorine Dioxide in N‑Nitrosodimethylamine Formation
    Article pubs.acs.org/est Role of Chlorine Dioxide in N‑Nitrosodimethylamine Formation from Oxidation of Model Amines † ‡ † § Wenhui Gan, Tom Bond, Xin Yang,*, and Paul Westerhoff † SYSU-HKUST Research Center for Innovative Environmental Technology, School of Environmental Science and Engineering, Sun Yat-sen University, Guangzhou 510275, China ‡ Department of Civil and Environmental Engineering, Imperial College London, London SW7 2AZ, United Kingdom § School of Sustainable Engineering and the Built Environment, Arizona State University, Tempe, Arizona 85287-3005, United States *S Supporting Information ABSTRACT: N-Nitrosodimethylamine (NDMA) is an emerging disinfection byproduct, and we show that use of chlorine dioxide (ClO2) has the potential to increase NDMA formation in waters containing precursors with hydrazine moieties. NDMA formation was measured after oxidation of 13 amines by monochloramine and ClO2 and pretreatment with ClO2 followed by postmonochloramination. Daminozide, a plant growth regulator, was found to yield 5.01 ± 0.96% NDMA upon reaction with ClO2, although no NDMA was recorded during chloramination. The reaction rate was estimated to be ∼0.0085 s−1, and on the basis of our identification by mass spectrometry of the intermediates, the reaction likely proceeds via the hydrolytic release of unsymmetrical dimethylhydrazine (UDMH), with the hydrazine structure a key intermediate in NDMA formation. The presence fi − of UDMH was con rmed by gas chromatography mass spectrometry analysis. For 10 of the 13 compounds, ClO2 preoxidation reduced NDMA yields compared with monochloramination alone, which is explained by our measured release of dimethylamine. This work shows potential preoxidation strategies to control NDMA formation may not impact all organic precursors uniformly, so differences might be source specific depending upon the occurrence of different precursors in source waters.
    [Show full text]
  • 5. Potential for Human Exposure
    HYDRAZINES 119 5. POTENTIAL FOR HUMAN EXPOSURE 5.1 OVERVIEW Hydrazine and 1,1-dimethylhydrazine are industrial chemicals that enter the environment primarily by emissions from their use as aerospace fuels and from industrial facilities that manufacture, process, or use these chemicals. Treatment and disposal of wastes containing these chemicals also contribute to environmental concentrations. These chemicals may volatilize to the atmosphere from other media and may sorb to soils. These chemicals degrade rapidly in most environmental media. Oxidation is the dominant fate process, but biodegradation occurs in both water and soil at low contaminant concentrations. The half-lives in air range from less than 10 minutes to several hours, depending on ozone and hydroxyl radical concentrations. Half-lives in other media range up to several weeks, under various environmental conditions. Bioconcentration does occur, but biomagnification through the food chain is unlikely. Human exposure to hydrazine and 1,1-dimethylhydrazine is mainly in the workplace or in the vicinity of aerospace or industrial facilities or hazardous waste sites where contamination has been detected. These chemicals have not been detected in ambient air, water, or soil. Humans may also be exposed to small amounts of these chemicals by using tobacco products. Hydrazine has been found in at least 4 of the 1,430 current or former EPA National Priorities List (NPL) hazardous waste sites (HazDat 1996). 1,1 -Dimethylhydrazine and 1,2-dimethylhydrazine have been identified in at least 3 and 1 of these sites, respectively. However, the number of sites evaluated for these chemicals is not known. The frequency of these sites within the United States can be seen in Figure 5-1.
    [Show full text]
  • Daminozide (Alar) Breakdown During Thermal Processing of Cherry Products T0 Yield, Unsymmetrical Dimethyl— Hydrazine (Udmh)'." "
    .H I n , In»! , a?) 1 ,-~ / p”7’56 .. v] -. V 1")!" h ‘ ._. Illlllllllllllllllllllllllllllll 11‘ l‘lllllllllllllllll 3 129300 r \ LIBRARY Ilium“. State University This is to certify that the dissertation entitled DAMINOZIDE (ALAR) BREAKDOWN DURING THERMAL PROCESSING OF CHERRY PRODUCTS T0 YIELD, UNSYMMETRICAL DIMETHYL— HYDRAZINE (UDMH)'." " presented by CHARLES RICHARD SANTERRE has been accepted towards fulfillment of the requirements for Ph.D. degmin FOOD SCIENCE & ENVIRONMENTAL TOX. Date March 24, 1989 MS U is an Affirmative Action/Equal Opportunity Institution 0-1277 1 ‘~.¢ O’Ntw , record. PLACE IN RETURN isfleckout from your TO AVOID FINES retur on or b ore date d . DATE DUE-ADA15- I DATE DUE Q MSU I. An Affirmative Action/Equal Opportunity Institution email-HM DAMINOZIDE (ALAR) BREAKDOWN DURING THERMAL PROCESSING OF CHERRY PRODUCTS TO YIELD, UNSYMMETRICAL DIMETHYLHYDRAZINE (UDMH). by Charles Richard Santerre A DISSERTATION Submitted to Michigan State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY Department of Food Science a Human Nutrition 1989 “‘3X 5072 ABSTRACT DAMINOZIDE (ALAR) BREAKDOWN DURING THERMAL PROCESSING OF CHERRY PRODUCTS TO YIELD, UNSYMMETRICAL DIMETHYLHYDRAZINE (UDMH). By Charles Richard Santerre Daminozide is applied to tart and sweet cherries to improve fruit color, texture and abscission at harvest. This growth retardant is a system ic compound which is distributed throughout the fruit matrix. Thermal processing of fruit containing daminozide produces a hydrolysis product, unsymmetrical dimethylhydrazine (UDMH), which is a cancer suspect agent. Daminozide was added to a 50 mM NaH2P04-24% sucrose solution at 12.5 ppm (w/w) to determine the influence of heating, pH and processing conditions on hydrolysis of daminozide to UDMH.
    [Show full text]
  • Gardner-Webb University Chemical Hygiene Plan Contents
    Gardner‐Webb University Chemical Hygiene Plan Date Issued: Prepared by: Venita Totten, Ph.D. Department of Natural Sciences Approved By: David Wacaster, Director Environmental & Occupational Safety Approved By: Gardner-Webb University Chemical Hygiene Plan Contents Introduction Definitions Scope and Applications Responsibilities Safe Laboratory Practices Good Laboratory Practices Guidelines for Chemical Use in Teaching Laboratories Food, Beverages & Chemical/Biological Contamination Housekeeping Glassware Personal Protective Equipment Warning Signs/MSDS Unattended Operations Working Alone Hazardous Waste Management Guidelines Hazardous Material Handling and Storage General Guidelines Preventing Exposure to Hazardous Chemicals Procurement Transport Chemical Storage Labeling Inventory Control Compressed Gases Controlling Specific Chemical Hazards and Exposures Corrosives Flammable and Combustible Liquids Carcinogens, Reproductive Toxins, and Acutely Toxic Chemicals Controlling Potential Exposure to Hazardous Chemicals Inhalation Hazards Skin/Eye Contact Hazards Ingestion Hazards Injection Hazards Chemical Hygiene Plan Page 2 Gardner-Webb University Chemical Hygiene Plan Personal Safety Major Hazard Emergencies Minor Hazard Emergencies Chemical Spills Fume Hoods and Other Engineering Controls Biological Safety Training and Information Medical Consultation Planning for Emergencies Appendices Appendix A Laboratory Standard Appendix B List of Acutely Toxic Chemicals Appendix C List of Select and Suspected Carcinogens Appendix D List of Reproductive Hazards Appendix E P-Listed Chemicals Appendix F Chemical Use Planning Form Appendix G Hazard Assessment & PPE Chemical Hygiene Plan Page 3 Gardner-Webb University Chemical Hygiene Plan Introduction and Purpose The Department of Natural Sciences at Gardner-Webb University has developed this Chemical Hygiene Plan to define work practices and procedures to help ensure that all personnel are protected from health and safety hazards associated with the chemicals with which they work.
    [Show full text]
  • Chemical Hygiene Plan
    Chemical Hygiene Plan Document Number: EHS-DOC600.02 Chemical Hygiene Plan Table of Contents 1.0 BACKGROUND ......................................................................................................................... 5 1.1 REGULATORY STANDARDS .............................................................................................................. 5 1.2 FLORIDA INTERNATIONAL UNIVERSITY LABORATORY SAFETY STANDARD OPERATING PROCEDURES ............................................................................................................................................... 5 1.3 PLAN DEVELOPMENT, MAINTENANCE, AND REVISION .................................................................. 6 2.0 INTRODUCTION ....................................................................................................................... 7 2.1 PURPOSE ......................................................................................................................................... 7 2.2 SCOPE .............................................................................................................................................. 7 2.3 PROGRAM ADMINISTRATION RESPONSIBILITY AND ACCOUNTABILITY ......................................... 8 2.4 GENERAL LABORATORY SAFETY CONCEPTS .................................................................................. 10 3.0 HEALTH AND SAFETY TRAINING REQUIREMENTS .................................................................... 15 3.1 EMPLOYEE RIGHT-TO-KNOW STANDARD ....................................................................................
    [Show full text]