Managing Hypochlorite to Reduce Chlorate Formation: a Utility Case Study
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Sodium Chlorate Process Liquor De-Chromed SN
SAFETY DATA SHEET This SDS adheres to the standards and regulatory requirements of the United States and may not meet the regulatory requirements in other countries. 1. Identification Product identifier Sodium Chlorate Process Liquor De-chromed SN Other means of identification De-chromed blend of Crystallizer Feed Liquor and Mother Liquor, NaClO3 Recommended use For internal transfer between ERCO Worldwide sodium chlorate manufacturing facilities for process purposes Recommended restrictions None known Manufacturer/Importer/Supplier/Distributor information Manufacturer Company name ERCO Worldwide Address 335 Carlingview Drive Unit 1 Etobicoke, M9W 5G8 Canada Telephone Information #: (416) 239-7111 (M- F: 8:00 am – 5:00pm EST) Website http://www.ercoworldwide.com E-mail [email protected] Emergency phone number Canada & USA: 1-800-424-9300 (CHEMTREC) Supplier Refer to Manufacturer 2. Hazard(s) Identification Physical hazards Oxidizing liquids Category 2 Health hazards Acute toxicity, oral Category 4 Environmental hazards Not currently regulated by OSHA, refer to Section 12 for additional information. OSHA defined hazards This mixture does not meet the classification criteria according to OSHA HazCom 2012. Label elements Signal word Danger Hazard statement May intensify fire; oxidizer. Harmful if swallowed. Page 1 of 15 Issue Date: 11/18/2020 Sodium Chlorate Process Liquor De-chromed SN Precautionary statement Prevention Keep away from heat, hot surfaces, sparks, open flames and other ignition sources. No smoking. Keep away from clothing and other combustible materials. Wear protective gloves, protective clothing, eye protection, face protection. Response IF ON SKIN: Wash with plenty of water. Take off contaminated clothing and wash it before reuse. In case of fire: Use water to extinguish. -
Mechanism of Action of Sodium Hypochlorite ISSN 0103-6440113
Braz Dent J (2002) 13(2): 113-117 Mechanism of action of sodium hypochlorite ISSN 0103-6440113 Mechanism of Action of Sodium Hypochlorite Carlos ESTRELA1 Cyntia R.A. ESTRELA1 Eduardo Luis BARBIN2 Júlio César E. SPANÓ2 Melissa A. MARCHESAN2 Jesus D. PÉCORA2 1Faculty of Dentistry, Federal University of Goiás, Goiânia, GO, Brazil 2Faculty of Dentistry of Ribeirão Preto, University of São Paulo, Ribeirão Preto, SP, Brazil The choice of an irrigating solution for use in infected root canals requires previous knowledge of the microorganisms responsible for the infectious process as well as the properties of different irrigating solutions. Complex internal anatomy, host defenses and microorganism virulence are important factors in the treatment of teeth with asymptomatic apical periodontitis. Irrigating solutions must have expressive antimicrobial action and tissue dissolution capacity. Sodium hypochlorite is the most used irrigating solution in endodontics, because its mechanism of action causes biosynthetic alterations in cellular metabolism and phospholipid destruction, formation of chloramines that interfere in cellular metabolism, oxidative action with irreversible enzymatic inactivation in bacteria, and lipid and fatty acid degradation. The aim of this work is to discuss the mechanism of action of sodium hypochlorite based on its antimicrobial and physico-chemical properties. Key Words: sodium hypochlorite, irrigating solution, intracanal dressing. INTRODUCTION microbial agent to the infected site, adequate concen- tration of the agent, -
Production of Hexavalent Chromium for Use in Chlorate Cells
Europaisches Patentamt J European Patent Office © Publication number: 0 266 128 A2 Office europeen des brevets EUROPEAN PATENT APPLICATION © Application number: 87309335.5 © Int. CIA C25B 1/26 @ Date of filing: 22.10.87 ® Priority: 29.10.86 CA 521737 © Applicant: Tenneco Canada Inc. 2 Gibbs Road © Date of publication of application: Islington OntarioM9B 1R1(CA) 04.05.88 Bulletin 88/18 0 Inventor: Dobosz, Leszek Michal © Designated Contracting States: 68 MacDonald Street CH ES FR LI SE Toronto Ontario M8V 1Y4(CA) © Representative: Hamilton, Raymond et al c/o Albright & Wilson Limited 1 Knightsbridge Green London SW1X 7QD(GB) © Production of hexavalent chromium for use in chlorate cells. © By-product hypochlorite from the electrolytic production of chlorates, notably sodium chlorate, is used to form hexavalent chromium for use in the electrolysis process by oxidation of trivalent chromium compounds by the hypochlorite. The hypochlorite maybe the condensate produced by treatment of the chlorate cell by-product gas stream and/or present in the cell liquor. < 00 CO CO (VI a. UJ Xerox Copy Centre 0 266 128 PRODUCTION OF HEXAVALENT CHROMIUM FOR USE IN CHLORATE CELLLS The present invention relates to the fomation of hexavalent chromium useful in the electrolytic production of aqueous chlorate solutions. An aqueous solution of sodium chlorate and sodium chloride is conventionally produced by the electrolysis of aqueous sodium chloride in diaphragmless electrolytic cells. The extent of electrolysis is 5 controlled to produce an effluent from the cell in which the sodium chlorate and sodium chloride have the desired ratio, usually in the range (expressed as a weight ratio) of about 1 :1 to about 20:1 and preferably in the range of about 2:1 to about 15:1. -
Disinfection Session Objectives
Disinfection Session Objectives • To introduce the principal disinfectants that may be used and highlight key advantages and disadvantages of each • To emphasise the use of chlorination for routine disinfection. • To describe the process of chlorination and discuss the concepts of breakpoint chlorination, chlorine demand and outline basic chlorine chemistry. • To discuss the types of chlorine available and how these may be used for routine disinfection. WHO SEMINAR PACK FOR DRINKING-WATER QUALITY Disinfection Introduction All water supplies should be disinfected. This is aimed both at inactivating remaining bacteria before distribution and providing a residual disinfectant to inactivate bacteria introduced by any subsequent ingress of contaminated water during storage or distribution. At present, the principal disinfectant used worldwide is chlorine, although alternatives are being increasingly investigated and process such as ozonation are becoming more common. Chlorine is generally the disinfectant of choice as it is reasonably efficient, cheap and easy to handle. In all but the smallest water treatment plants, chlorine is added to water as either in aqueous solution (calcium hypochlorite or sodium hypochlorite) or chlorine gas. Smaller supplies may use tablets of hypochlorite. Other disinfectants include ozone, ultraviolet light and iodine. These all have disadvantages. UV is not a particularly effective disinfectant and it is difficult to expose water for sufficient time for disinfection to be effective. Neither ozone or UV provide a residual disinfectant and therefore offer no protection against recontamination in distribution. To overcome this, in some water supplies booster ozonation stations are set up along the distribution network. Both iodine and ozone are carcinogenic. There are also significant health and safety concerns, for operators, regarding the generation and application of ozone and chlorine (especially in the gaseous form). -
Sodium Chlorite Neutralization
® Basic Chemicals Sodium Chlorite Neutralization Introduction that this reaction is exothermic and liberates a If sodium chlorite is spilled or becomes a waste, significant amount of heat (H). it must be disposed of in accordance with local, state, and Federal regulations by a NPDES NaClO2 + 2Na2SO3 2Na2SO4 + NaCl permitted out-fall or in a permitted hazardous 90.45g + 2(126.04g) 2(142.04g) + 58.44g waste treatment, storage, and disposal facility. H = -168 kcal/mole NaClO2 Due to the reactivity of sodium chlorite, neutralization for disposal purposes should be For example, when starting with a 5% NaClO2 avoided whenever possible. Where permitted, solution, the heat generated from this reaction the preferred method for handling sodium could theoretically raise the temperature of the chlorite spills and waste is by dilution, as solution by 81C (146F). Adequate dilution, discussed in the OxyChem Safety Data Sheet thorough mixing and a slow rate of reaction are (SDS) for sodium chlorite in Section 6, important factors in controlling the temperature (Accidental Release Measures). Sodium chlorite increase (T). neutralization procedures must be carried out only by properly trained personnel wearing Procedure appropriate protective equipment. The complete neutralization procedure involves three sequential steps: dilution, chlorite Reaction Considerations reduction, and alkali neutralization. The dilution If a specific situation requires sodium chlorite to step lowers the strength of the sodium chlorite be neutralized, the chlorite must first be reduced solution to 5% or less; the reduction step reacts by a reaction with sodium sulfite. The use of the diluted chlorite solution with sodium sulfite to sodium sulfite is recommended over other produce a sulfate solution, and the neutralization reducing agents such as sodium thiosulfate step reduces the pH of the alkaline sulfate (Na2S2O3), sodium bisulfite (NaHSO3), and solution from approximately 12 to 4-5. -
Guidelines for Drinking-Water Quality, Fourth Edition
12. CHEMICAL FACT SHEETS Assessment date 1993 Principal reference WHO (2003) Chlorine in drinking-water In humans and experimental animals exposed to chlorine in drinking-water, no specific adverse treatment-related effects have been observed. IARC has classified h ypochlorite in Group 3 (not classifiable as to its carcinogenicity to humans). Chlorite and chlorate Chlorite and chlorate are disinfection by-products resulting from the use of chlorine dioxide as a disinfectant and for odour and taste control in water. Chlorine dioxide is also used as a bleaching agent for cellulose, paper pulp, flour and oils. Sodium chlorite and sodium chlorate are both used in the production of chlorine dioxide as well as for other commercial purposes. Chlorine dioxide rapidly decomposes into chlorite, chlorate and chloride ions in treated water, chlorite being the predominant species; this reaction is favoured by alkaline conditions. The major route of environmental ex- posure to chlorine dioxide, sodium chlorite and sodium chlorate is through drinking- water. Chlorate is also formed in sodium hypochlorite solution that is stored for long periods, particularly at high ambient temperatures. Provisional guideline values Chlorite: 0.7 mg/l (700 µg/l) Chlorate: 0.7 mg/l (700 µg/l) The guideline values for chlorite and chlorate are designated as provisional because use of chlorine dioxide as a disinfectant may result in the chlorite and chlorate guideline values being exceeded, and difficulties in meeting the guideline value must never be a reason for compromising adequate disinfection. Occurrence Levels of chlorite in water reported in one study ranged from 3.2 to 7.0 mg/l; however, the combined levels will not exceed the dose of chlorine dioxide applied. -
Sodium Hypochlorite
SODIUM HYPOCHLORITE What is SODIUM HYPOCHLORITE? Sodium hypochlorite is a liquid with an odor of chlorine. Usually it is clear but some solutions are greenish to yellow in color. Other names for sodium hypochlorite include Clorox , bleach, liquid bleach, sodium oxychloride, Javex, antiformin, showchlon, Chlorox, B-K, Carrel-Dakin Solution, Chloros, Dakin’s Solution, hychlorite, Javelle Water, Mera Industries 2MOm≥B, Milton, modified Dakin’s Solution, Piochlor, and 13% active chlorine. Where can sodium hypochlorite be found and how is it used? Sodium hypochlorite is mainly used as a bleaching agent or disinfectant. A disinfectant kills bacteria that can carry diseases. It is found in consumer and commercial bleaches, cleaning solutions, and disinfectants for drinking water, wastewater and swimming pools. How can people be exposed to sodium hypochlorite? You could be exposed to sodium hypochlorite through: Breathing fumes while using products containing sodium hypochlorite. Drinking water from public drinking water supplies where these chemicals were added to kill bacteria. You could also be exposed by drinking sodium hypochlorite by accident. Touching sodium hypochlorite if gloves are not worn when using products containing it. Eye Contact by splashing sodium hypochlorite during use. People who work where sodium hypochlorite is used to bleach paper and textiles may have slightly higher levels of exposure in all of the above areas. How does sodium hypochlorite work and how can it affect my health? Sodium hypochlorite is a corrosive substance, meaning that it will eat away at materials it contacts. Accidental sodium hypochlorite poisoning can be deadly. Severe injuries can occur to the mouth, throat, esophagus and stomach. -
Nitrogen, Ammonia, Colorimetry, Salicylate-Hypochlorite, Automated-Segmented Flow
Nitrogen, ammonia, colorimetry, salicylate-hypochlorite, automated-segmented flow Parameters and Codes: Nitrogen, ammonia, dissolved, I-2522-90 (mg/L as N): 00608 Nitrogen, ammonia, total-in-bottom-material, I-6522-90 (mg/L as N): 00611 1. Application 1.1 This method is used to analyze samples of surface, domestic, and industrial water, and brines containing from 0.01 to 1.5 mg/L of ammonia-nitrogen. Concentrations greater than 1.50 mg/L must be diluted. This modified method was implemented in the National Water Quality Laboratory in March 1988. 1.2 This method also is used to determine concentrations of ammonia-nitrogen in samples of bottom material containing at least 0.2 mg/kg NH3-N. Prepared sample solutions containing more than 1.5 mg/L NH3-N need to be diluted. 1.3 Sodium ion is a good replacement for ammonium ion in the slow-exchange positions of soil minerals (Jackson, 1958). Bottom material is treated with an acidified sodium chloride solution, and the resulting mixture is allowed to settle and then decanted to obtain a clear supernatant solution for analysis. 2. Summary of method Ammonia reacts with salicylate and hypochlorite ions in the presence of ferricyanide ions to form the salicylic acid analog of indophenol blue (Reardon and others, 1966; Patton and Crouch, 1977; Harfmann and Crouch, 1989). The resulting color is directly proportional to the concentration of ammonia present. 3. Interferences 3.1 Sulfide interferes. Bromide and nitrite can interfere. Calcium and magnesium in highly alkaline waters (pH greater than 13.6) can exceed the ability of the tartrate to complex both ions. -
Dangers of Unspent Aircraft Oxygen Generators
Safety Advisory Dangers of Unspent Aircraft Oxygen Generators U.S. Chemical Safety and Hazard Investigation Board No. 2007-I-NC-01-SA | June 2007 Key Message This Safety Advisory is issued to alert aircraft maintenance and hazardous waste facility personnel to the hazards associated with the transportation and storage of expired, unspent aircraft chemical oxygen generators. Aircraft oxygen generators are dangerous devices that, if mishandled, can cause fires, property damage, and personal injury. Aircraft oxygen generators that have exceeded their service life should be expended before shipping by any transport mode. Introduction On October 5, 2006, at about 10 pm, a fire occurred at the EQ Industrial Services (EQ) hazardous waste treatment, storage, and disposal facility in Apex, North Carolina. The fire resulted in the evacuation of thousands of Apex residents and the complete destruction of the hazardous waste building at EQ’s Apex facility. The U.S. Chemical Safety and Hazard Investigation Board (CSB) investigation concluded that aircraft oxygen generators most likely contributed to the rapid spread of the fire to other areas in the EQ facility. The CSB issues this Safety Advisory to focus attention on the need for aircraft maintenance facilities to expend chemical oxygen generators that have exceeded their service life, and for hazardous waste facility operators and shippers to exercise due care when handling unspent chemical oxygen generators. Incident Description At about 10 pm on October 5, 2006, a citizen driving past the EQ facility in Apex, North Carolina, called 911 when he saw a plume of smoke and smelled a strong chlorine odor coming from the facility. -
COVID-19 Environmental Cleaning and Disinfectants for Clinic
Coronavirus COVID-19 BC Centre for Disease Control | BC Ministry of Health Environmental Cleaning and Disinfectants for Health-Care and Clinic Settings Cleaning: the physical removal of visible soiling (e.g., dust, soil, blood, mucus). Cleaning removes, rather than kills, viruses and bacteria. It is done with water, detergents, and steady friction from cleaning cloth. Disinfection: the killing of viruses and bacteria. A disinfectant is only applied to objects; never on the human body. All visibly soiled surfaces should be cleaned before disinfection. Environmental cleaning for the COVID-19 virus is the same as for other common viruses. Cleaning products and disinfectants that are regularly used in hospitals and health-care settings are strong enough to deactivate coronaviruses and prevent their spread. Cleaning of visibly soiled surfaces followed by disinfection is recommended for the prevention of COVID-19 and other viral respiratory illnesses. Suggested cleaning and disinfecting frequencies for health-care and clinic settings: Type of surface Frequency 1. Shared equipment IN BETWEEN PATIENTS otoscopes, baby scales, tables and exam beds 2. Frequently-touched surfaces Examples: medical equipment, door knobs, light AT LEAST TWICE A DAY switches, telephones, keyboards, mice, pens, charts, cell phones, toys, bathrooms 3. General cleaning of procedure / exam rooms AT LEAST ONCE A DAY For electronic equipment please comply with manufacturer’s instructions in order to meet warranty requirements 06.02.21 Coronavirus COVID-19 BC Centre for Disease Control | BC Ministry of Health Environmental Cleaning and Disinfectants for Health-Care and Clinic Settings The list of common disinfectants below is provided as a guide to choosing products. -
Perchlorate in Sodium Hypochlorite
emerging issues BY PETER GREINER, CLIF MCLELLAN, DALE BENNETT, AND ANGIE EWING Occurrence of perchlorate in sodium hypochlorite RESPONDING TO THE DETECTION erchlorate is both a synthetic and a naturally occurring chemical. Most of the perchlorate that is manufactured in the United States OF PERCHLORATE IN SODIUM is used as the primary ingredient of solid rocket propellant. Wastes HYPOCHLORITE BY THE from the manufacture and improper disposal of perchlorate-con- taining chemicals are increasingly being discovered in soil and water MASSACHUSETTS DEPARTMENT P (USEPA, 2007). OF ENVIRONMENTAL An additional source of perchlorate in drinking water has been found to occur through the use of sodium hypochlorite. The Massachusetts Department PROTECTION, of Environmental Protection (MDEP) has reported that significant levels of NSF INTERNATIONAL SURVEYED perchlorate can be detected in sodium hypochlorite samples that have aged for a few weeks (MDEP, 2005). Sodium hypochlorite as delivered to one utility FOR THE CONTAMINANT had a perchlorate concentration of 0.2 µg/L in the product, but the level of IN DRINKING WATER TREATMENT perchlorate rose to 6,750 µg/L after the product had aged for 26 days. CHEMICALS FROM PRODUCTION INVESTIGATION OF WATER TREATMENT CHEMICALS BEGAN IN 2005 FACILITIES ACROSS In 2005 NSF International began analyzing samples of drinking water treat- ment chemicals for the contaminant perchlorate. These samples were collected THE UNITED STATES as part of the annual testing requirement to support NSF certification of the AND CANADA. treatment chemical to NSF/American National Standards Institute Standard 60: Drinking Water Treatment Chemicals—Health Effects (NSF/ANSI, 2005). Samples collected included not only sodium hypochlorite but other types of chemicals as well. -
Six-Year Review 3 Technical Support Document for Chlorate
Six-Year Review 3 Technical Support Document for Chlorate Office of Water (4607M) EPA-810-R-16-013 December 2016 Disclaimer This document is not a regulation. It is not legally enforceable, and does not confer legal rights or impose legal obligations on any party, including EPA, states, or the regulated community. While EPA has made every effort to ensure the accuracy of any references to statutory or regulatory requirements, the obligations of the interested stakeholders are determined by statutes, regulations or other legally binding requirements, not this document. In the event of a conflict between the information in this document and any statute or regulation, this document would not be controlling. This page intentionally left blank. Table of Contents 1 Introduction ................................................................................................................. 1-1 2 Contaminant Background .......................................................................................... 2-1 2.1 Chemical and Physical Properties ................................................................................. 2-1 2.2 Production, Use and Release ......................................................................................... 2-2 2.2.1 Commercial Production and Use in Industry and Agriculture ........................... 2-2 2.2.2 Incidental Production and Release ...................................................................... 2-6 2.3 Environmental Fate ......................................................................................................