Haloacetic Acids Found As Water Disinfection By-Products
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APPENDIX G Acid Dissociation Constants
harxxxxx_App-G.qxd 3/8/10 1:34 PM Page AP11 APPENDIX G Acid Dissociation Constants § ϭ 0.1 M 0 ؍ (Ionic strength ( † ‡ † Name Structure* pKa Ka pKa ϫ Ϫ5 Acetic acid CH3CO2H 4.756 1.75 10 4.56 (ethanoic acid) N ϩ H3 ϫ Ϫ3 Alanine CHCH3 2.344 (CO2H) 4.53 10 2.33 ϫ Ϫ10 9.868 (NH3) 1.36 10 9.71 CO2H ϩ Ϫ5 Aminobenzene NH3 4.601 2.51 ϫ 10 4.64 (aniline) ϪO SNϩ Ϫ4 4-Aminobenzenesulfonic acid 3 H3 3.232 5.86 ϫ 10 3.01 (sulfanilic acid) ϩ NH3 ϫ Ϫ3 2-Aminobenzoic acid 2.08 (CO2H) 8.3 10 2.01 ϫ Ϫ5 (anthranilic acid) 4.96 (NH3) 1.10 10 4.78 CO2H ϩ 2-Aminoethanethiol HSCH2CH2NH3 —— 8.21 (SH) (2-mercaptoethylamine) —— 10.73 (NH3) ϩ ϫ Ϫ10 2-Aminoethanol HOCH2CH2NH3 9.498 3.18 10 9.52 (ethanolamine) O H ϫ Ϫ5 4.70 (NH3) (20°) 2.0 10 4.74 2-Aminophenol Ϫ 9.97 (OH) (20°) 1.05 ϫ 10 10 9.87 ϩ NH3 ϩ ϫ Ϫ10 Ammonia NH4 9.245 5.69 10 9.26 N ϩ H3 N ϩ H2 ϫ Ϫ2 1.823 (CO2H) 1.50 10 2.03 CHCH CH CH NHC ϫ Ϫ9 Arginine 2 2 2 8.991 (NH3) 1.02 10 9.00 NH —— (NH2) —— (12.1) CO2H 2 O Ϫ 2.24 5.8 ϫ 10 3 2.15 Ϫ Arsenic acid HO As OH 6.96 1.10 ϫ 10 7 6.65 Ϫ (hydrogen arsenate) (11.50) 3.2 ϫ 10 12 (11.18) OH ϫ Ϫ10 Arsenious acid As(OH)3 9.29 5.1 10 9.14 (hydrogen arsenite) N ϩ O H3 Asparagine CHCH2CNH2 —— —— 2.16 (CO2H) —— —— 8.73 (NH3) CO2H *Each acid is written in its protonated form. -
Evaluating Analytical Methods for Detecting Unknown Chemicals in Recycled Water
PROJECT NO. 4992 Evaluating Analytical Methods for Detecting Unknown Chemicals in Recycled Water Evaluating Analytical Methods for Detecting Unknown Chemicals in Recycled Water Prepared by: Keith A. Maruya Charles S. Wong Southern California Coastal Water Research Project Authority 2020 The Water Research Foundation (WRF) is a nonprofit (501c3) organization which provides a unified source for One Water research and a strong presence in relationships with partner organizations, government and regulatory agencies, and Congress. The foundation conducts research in all areas of drinking water, wastewater, stormwater, and water reuse. The Water Research Foundation’s research portfolio is valued at over $700 million. The Foundation plays an important role in the translation and dissemination of applied research, technology demonstration, and education, through creation of research‐based educational tools and technology exchange opportunities. WRF serves as a leader and model for collaboration across the water industry and its materials are used to inform policymakers and the public on the science, economic value, and environmental benefits of using and recovering resources found in water, as well as the feasibility of implementing new technologies. For more information, contact: The Water Research Foundation Alexandria, VA Office Denver, CO Office 1199 North Fairfax Street, Suite 900 6666 West Quincy Avenue Alexandria, VA 22314‐1445 Denver, Colorado 80235‐3098 Tel: 571.384.2100 Tel: 303.347.6100 www.waterrf.org [email protected] ©Copyright 2020 by The Water Research Foundation. All rights reserved. Permission to copy must be obtained from The Water Research Foundation. WRF ISBN: 978‐1‐60573‐503‐0 WRF Project Number: 4992 This report was prepared by the organization(s) named below as an account of work sponsored by The Water Research Foundation. -
Determination of Haloacetic Acids in Water Using IC-ESI-MS/MS
Application Note 217 Note Application Determination of Haloacetic Acids in Water Using IC-ESI-MS/MS Rosanne Slingsby, Charanjit Saini, and Chris Pohl Thermo Fisher Scientific, Sunnyvale, CA, USA Introduction The determination of the chloro-, bromo-, and mixed This method allows separation and detection of sub-µg/L haloacetic acids in waters destined for human consump- levels of nine haloacetic acids (HAAs) in high-ionic tion, including drinking water and swimming pool water, strength matrices. Using this method, the analytes are has been reported using a variety of analytical techniques.3 separated from chloride, sulfate, nitrate, bromide, and U.S. EPA Methods 552.2 and 552.3 use acidic methanol bicarbonate, and detected using a triple quadrupole mass derivatization followed by gas chromatography with spectrometer with an electrospray interface. Quantifica- electron capture detection.4 This method is both labor- tion is achieved using internal standards. intensive and time-consuming. Bruzzoniti5 recently published a table summarizing the existing IC columns Haloacetic acids occur in drinking water during the and methods used for HAAs analysis, including this disinfection process as a result of the reaction between method, which uses the Thermo Scientific™ Dionex™ chlorine and natural organic materials such as humic and IonPac™ AS24 column. Asami6 used offline sample fulvic acids.1,2 The iodoacids (for example, iodoacetic pretreatment with external standard calibration and acid) are much less stable and are not included in this MS/MS detection for calibration of haloacetic acids and analysis. When bromide is present in the water, bromoace- oxyhalides, using perchlorate as an internal standard. tic acids and mixed chloro- and bromoacetic acids can Only the method using the Dionex IonPac AS24 column also be generated. -
Justin Pals.Pdf
MECHANISMS OF MONOHALOGENATED ACETIC ACID INDUCED GENOMIC DNA DAMAGE BY JUSTIN A. PALS DISSERTATION Submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy in Crop Sciences in the Graduate College of the University of Illinois at Urbana-Champaign, 2014 Urbana, Illinois Doctoral Committee: Professor Michael J. Plewa, Chair Professor Benito J. Mariñas Professor A. Layne Rayburn Brian K. Miller, Director of Illinois-Indiana Sea Grant ABSTRACT Disinfection of drinking water stands among the greatest public health achievements in human history. Killing or inactivation of pathogenic microbes by chemical oxidants such as chlorine, chloramine, or ozone have greatly reduced incidence of waterborne diseases. However, the disinfectant also reacts with organic and inorganic matter in the source water and generates a mixture of toxic disinfection byproducts (DBPs) as an unintended consequence. Since they were first discovered in 1974, over 600 individual DBPs have been detected in disinfected water. Exposure to DBPs is associated with increased risks for developing cancers of the colon, rectum, and bladder, and also for adverse pregnancy outcomes including small for gestational age and congenital malformations. While individual DBPs are teratogenic or carcinogenic, because they are formed at low concentrations during disinfection, it is unlikely that any one DBP can account for these increased risks. While genotoxicity and oxidative stress have been suggested, the mechanisms connecting DBP exposures to adverse health and pregnancy outcomes remain unknown. Investigating mechanisms of toxicity for individual, or classes of DBPs will provide a better understanding of how multiple DBPs interact to generate adverse health and pregnancy outcomes. Monohalogenated acetic acids (monoHAAs) iodoacetic acid (IAA), bromoacetic acid (BAA), and chloroacetic acid (CAA) are genotoxic and mutagenic with the consistent rank order of toxicity of IAA > BAA > CAA. -
Preparation and Isolation of the S-Carboxymethy L Derivative Chains of Human Fibrinogen
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Elsevier - Publisher Connector Volume 14, number 1 FEBSLETTERS April 1971 PREPARATION AND ISOLATION OF THE S-CARBOXYMETHY L DERIVATIVE CHAINS OF HUMAN FIBRINOGEN Genesio MURANO, Bjorn WIMAN, Margareta BLOMBACK and Birger BLOMBACK Dept. of Blood Coagulation Research, Karolinska Institute, Stockholm, Sweden Received 1 March 1971 1. Introduction Amersham, England) Lot No. B 10, specific activity: 50-l 50 mCi/mmole, was diluted appropriately with Fibrinogen is composed of three pairs of polypeptide carrier iodoacetic acid before use. chains: o(A), /3(B), and y [ 1,2] . Fibrinopeptides A 3H-Iodoacetic acid-carrier mixture was prepared and B are cleaved off the a(A) and P(B) chains respecti- fresh by mixing 4 ml of 1 M iodoacetic acid carrier vely by thrombin. The resulting product is fibrin [3,4]. (186 mg/mI of 0.1 N NaOH) with 6 ml of 2-j H-iodo- Sulfitolysis of fibrinogen results in the cleavage of the acetic acid (1 mCi/ml of 0.1 N NaOH). disulfide bridges [5] , and the resulting S-sulfo chain Carboxymethyl cellulose (CM-52) was precycled derivatives have been separated by paper [ 51, starch as recommended by the manufacturer (H. Reeve gel electrophoresis [6] and column chromatography Angel and Co., London, England). [S, 71. More recently, the S-sulfo chain derivatives Radioactivity measurements were performed with from bovine [8] and human [9] fibrinogen have been a Beckman liquid scintillation system (CPM 200). isolated on carboxymethyl cellulose using a stepwise N-Terminal sequence amino acid analysis: The [8] and gradient [9] sodium acetate buffer system. -
Dissociation Constants of Organic Acids and Bases
DISSOCIATION CONSTANTS OF ORGANIC ACIDS AND BASES This table lists the dissociation (ionization) constants of over pKa + pKb = pKwater = 14.00 (at 25°C) 1070 organic acids, bases, and amphoteric compounds. All data apply to dilute aqueous solutions and are presented as values of Compounds are listed by molecular formula in Hill order. pKa, which is defined as the negative of the logarithm of the equi- librium constant K for the reaction a References HA H+ + A- 1. Perrin, D. D., Dissociation Constants of Organic Bases in Aqueous i.e., Solution, Butterworths, London, 1965; Supplement, 1972. 2. Serjeant, E. P., and Dempsey, B., Ionization Constants of Organic Acids + - Ka = [H ][A ]/[HA] in Aqueous Solution, Pergamon, Oxford, 1979. 3. Albert, A., “Ionization Constants of Heterocyclic Substances”, in where [H+], etc. represent the concentrations of the respective Katritzky, A. R., Ed., Physical Methods in Heterocyclic Chemistry, - species in mol/L. It follows that pKa = pH + log[HA] – log[A ], so Academic Press, New York, 1963. 4. Sober, H.A., Ed., CRC Handbook of Biochemistry, CRC Press, Boca that a solution with 50% dissociation has pH equal to the pKa of the acid. Raton, FL, 1968. 5. Perrin, D. D., Dempsey, B., and Serjeant, E. P., pK Prediction for Data for bases are presented as pK values for the conjugate acid, a a Organic Acids and Bases, Chapman and Hall, London, 1981. i.e., for the reaction 6. Albert, A., and Serjeant, E. P., The Determination of Ionization + + Constants, Third Edition, Chapman and Hall, London, 1984. BH H + B 7. Budavari, S., Ed., The Merck Index, Twelth Edition, Merck & Co., Whitehouse Station, NJ, 1996. -
Faqs About the Haloacetic Acids Public Notice
FAQs About the Haloacetic Acids Public Notice BCWSA staff work diligently to deliver the highest quality drinking water to its customers. We invest in replacing and upgrading aging infrastructure and continuously make improvements to ensure that we meet upcoming water regulations. Sometimes circumstances beyond our control may affect the quality of the drinking water. On December 20, 2017 public notice was issued for one such instance. Below are some answers to some frequently asked questions about the public notice that was issued. Am I in the area affected by this public notice? If you receive water from BCWSA and received the public notice that was sent on December 20, 2017, then you are within the affected area. If you do not receive your drinking water from BCWSA, than you are not affected. If you receive your water from BCWSA but are in the New Hope area, you are not affected - the source of your water is a different supply and the public notice does not apply to you. If you are unsure if this notice applies to you, please call us at 215-343-2538 to determine if you are within the service area affected by this notice. Why is there a drinking water violation? Chlorine is used in the water supply to kill harmful bacteria and viruses. When the chlorine is added to the water, it combines with naturally occurring organic and inorganic materials present in the source water and forms chemicals called disinfection byproducts (DBPs). The EPA sets standards for controlling the levels of these DBPs, including Total Trihalomethanes (THMs) and Haloacetic Acids (HAAs). -
Monograph on Haloacetic Acids Found As Water Disinfection By-Products
REPORT ON CArcINOGENS MONOGRAPH ON HALOACETIC ACIDS FOUND AS WATER DISINFECTION BY-PRODUCTS ROC MONOGRAPH 12 MARCH 2018 Report on Carcinogens Monograph on Haloacetic Acids Found as Water Disinfection By-Products RoC Monograph 12 March 2018 National Toxicology Program Public Health Service U.S. Department of Health and Human Services ISSN: 2331-267X Research Triangle Park, North Carolina, USA RoC Monograph on Haloacetic Acids Foreword The National Toxicology Program (NTP), established in 1978, is an interagency program within the Public Health Service of the U.S. Department of Health and Human Services. Its activities are executed through a partnership of the National Institute for Occupational Safety and Health (part of the Centers for Disease Control and Prevention), the Food and Drug Administration (primarily at the National Center for Toxicological Research), and the National Institute of Environmental Health Sciences (part of the National Institutes of Health), where the program is administratively located. NTP offers a unique venue for the testing, research, and analysis of agents of concern to identify toxic and biological effects, provide information that strengthens the science base, and inform decisions by health regulatory and research agencies to safeguard public health. NTP also works to develop and apply new and improved methods and approaches that advance toxicology and better assess health effects from environmental exposures. The Report on Carcinogens Monograph series began in 2012. Report on Carcinogens Monographs present the cancer hazard evaluations of environmental agents, substances, mixtures, or exposure circumstances (collectively referred to as “substances”) under review for the Report on Carcinogens. The Report on Carcinogens is a congressionally mandated, science- based, public health document that provides a cumulative list of substances that pose a cancer hazard for people in the United States. -
Mechanisms of Monohalogenated Acetic Acid Induced Genomic Dna Damage
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Illinois Digital Environment for Access to Learning and Scholarship Repository MECHANISMS OF MONOHALOGENATED ACETIC ACID INDUCED GENOMIC DNA DAMAGE BY JUSTIN A. PALS DISSERTATION Submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy in Crop Sciences in the Graduate College of the University of Illinois at Urbana-Champaign, 2014 Urbana, Illinois Doctoral Committee: Professor Michael J. Plewa, Chair Professor Benito J. Mariñas Professor A. Layne Rayburn Brian K. Miller, Director of Illinois-Indiana Sea Grant ABSTRACT Disinfection of drinking water stands among the greatest public health achievements in human history. Killing or inactivation of pathogenic microbes by chemical oxidants such as chlorine, chloramine, or ozone have greatly reduced incidence of waterborne diseases. However, the disinfectant also reacts with organic and inorganic matter in the source water and generates a mixture of toxic disinfection byproducts (DBPs) as an unintended consequence. Since they were first discovered in 1974, over 600 individual DBPs have been detected in disinfected water. Exposure to DBPs is associated with increased risks for developing cancers of the colon, rectum, and bladder, and also for adverse pregnancy outcomes including small for gestational age and congenital malformations. While individual DBPs are teratogenic or carcinogenic, because they are formed at low concentrations during disinfection, it is unlikely that any one DBP can account for these increased risks. While genotoxicity and oxidative stress have been suggested, the mechanisms connecting DBP exposures to adverse health and pregnancy outcomes remain unknown. Investigating mechanisms of toxicity for individual, or classes of DBPs will provide a better understanding of how multiple DBPs interact to generate adverse health and pregnancy outcomes. -
European Union Risk Assessment Report
European Chemicals Bureau Institute for Health and Consumer Protection European Union Risk Assessment Report European Chemicals Bureau CAS No: 79-11-8 EINECS No: 201-178-4 Existing Substances monochloroacetic acid (MCAA) European monochloroacetic acid Union Risk Assessment Report Report Assessment Risk Union H O Cl C C ( MCAA OH ) H CAS: EC: 201-178-4 79-11-8 3rd Priority List Volume: 52 PL-3 EUR 21403 EN 52 European Union Risk Assessment Report MONOCHLOROACETIC ACID (MCAA) CAS-No.: 79-11-8 EINECS-No.: 201-178-4 RISK ASSESSMENT LEGAL NOTICE Neither the European Commission nor any person acting on behalf of the Commission is responsible for the use which might be made of the following information A great deal of additional information on the European Union is available on the Internet. It can be accessed through the Europa Server (http://europa.eu.int). Cataloguing data can be found at the end of this publication Luxembourg: Office for Official Publications of the European Communities, 2005 © European Communities, 2005 Reproduction is authorised provided the source is acknowledged. Printed in Italy MONOCHLOROACETIC ACID (MCAA) CAS No: 79-11-8 EINECS No: 201-178-4 RISK ASSESSMENT Final Report, 2005 The Netherlands Rapporteur for the risk evaluation of monochloroacetic acid is the Ministry of Housing, Spatial Planning and the Environment (VROM) in consultation with the Ministry of Social Affairs and Employment (SZW) and the Ministry of Public Health, Welfare and Sport (VWS). Responsible for the risk evaluation and subsequently for the contents of this report is the rapporteur. The scientific work on this report has been prepared by the Netherlands Organization for Applied Scientific Research (TNO) and the National Institute of Public Health and Environment (RIVM), by order of the rapporteur. -
Dichloroacetic Acid
pp359-402.qxd 11/10/2004 11:27 Page 359 DICHLOROACETIC ACID This substance was considered by a previous Working Group in February 1995 (IARC, 1995). Since that time, new data have become available, and these have been incorporated into the monograph and taken into consideration in the present evaluation. 1. Exposure Data 1.1 Chemical and physical data 1.1.1 Nomenclature Chem. Abstr. Serv. Reg. No.: 79-43-6 Deleted CAS Reg. No.: 42428-47-7 Chem. Abstr. Name: Dichloroacetic acid IUPAC Systematic Name: Dichloroacetic acid Synonyms: DCA; DCA (acid); dichloracetic acid; dichlorethanoic acid; dichloroetha- noic acid 1.1.2 Structural and molecular formulae and relative molecular mass Cl O H CCOH Cl C2H2Cl2O2 Relative molecular mass: 128.94 1.1.3 Chemical and physical properties of the pure substance (a) Description: Colourless, highly corrosive liquid (Koenig et al., 1986) (b) Boiling-point: 192 °C (Koenig et al., 1986) (c) Melting-point: 13.5 °C (freezing-point) (Koenig et al., 1986) (d) Density: 1.5634 at 20 °C/4 °C (Morris & Bost, 1991) –359– pp359-402.qxd 11/10/2004 11:27 Page 360 360 IARC MONOGRAPHS VOLUME 84 (e) Spectroscopy data: Infrared (prism [2806]), nuclear magnetic resonance [166] and mass spectral data have been reported (Weast & Astle, 1985) (f) Solubility: Miscible with water; soluble in organic solvents such as alcohols, ketones, hydrocarbons and chlorinated hydrocarbons (Koenig et al., 1986) (g) Volatility: Vapour pressure, 0.19 kPa at 20 °C (Koenig et al., 1986) × –2 (h) Stability: Dissociation constant (Ka), 5.14 10 (Morris & Bost, 1991) (i) Octanol/water partition coefficient (P): log P, 0.92 (Hansch et al., 1995) (j) Conversion factor: mg/m3 = 5.27 × ppma 1.1.4 Technical products and impurities Dichloroacetic acid is commercially available as a technical-grade liquid with the following typical specifications: purity, 98.0% min.; monochloroacetic acid, 0.2% max.; tri- chloroacetic acid, 1.0% max.; and water, 0.3% max. -
Haloacetic Acids
Oregon Department of Human Services Office of Environmental Public Health (503) 731-4030 Emergency 800 NE Oregon Street #604 (971) 673-0405 Portland, OR 97232-2162 (971) 673-0457 FAX (971) 673-0372 TTY-Nonvoice TECHNICAL BULLETIN HEALTH EFFECTS INFORMATION Prepared by: Department of Human Services ENVIRONMENTAL TOXICOLOGY SECTION DRINKING WATER PROGRAM Office of Environmental Public Health June 2004 HALOACETIC ACIDS For More Information Contact: Environmental Toxicology Section (971) 673-0440 Drinking Water Section (971) 673-0405 Technical Bulletin—Health Effects Information Haloacetic Acids Page 2 SYNONYMS Haloacetic acids include monochloracetic acid (MCAA), dichloroacetic acid (DCAA), trichloroacetic acid (TCAA), monobromoacetic acid (MBAA), dibromoacetic acid (DBAA), tribromoacetic acid (TBAA), bromochloroacetic acid (BCAA), bromodichloroacetic acid (BDCAA), and dibromochloroacetic acid (DBCAA).Of this chemical family only MCAA, DCAA, TCAA, MBAA and DBAA are currently regulated as drinking water contaminants. These five regulated HAAs are often referred to as HAA5. USES Most haloacetic acids in the environment are created as byproducts of chemical reactions or deliberately synthesized for industrial uses.They are used in fruit harvesting, as pesticides, as bacterial control agents, and in production of chemicals, pharmaceuticals and medicationsThey are also inadvertently formed during chlorination of water, in wood and paper bleaching industries, during sewage treatment processes. They are so widely produced, used and released that they can be found in most surface water and even in rainwater. The most significant source of haloacetic acids in drinking water is their production during disinfection with chlorine disinfectants. WHAT HAPPENS TO HALOACETIC ACIDS IN THE ENVIRONMENT Haloacetic acids are very soluble in water, and are quite stable chemically.They are difficult to destroy or remove from water.