DOCSLIB.ORG

Comparison of the Efficacies of Gaseous Ozone and Sodium Hypochlorite in Cleaning Stainless Steel Particles Fouled with Proteins

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Comparison of the Efficacies of Gaseous Ozone and Sodium Hypochlorite in Cleaning Stainless Steel Particles Fouled with Proteins Biocontrol Science, 2003, Vol. 8, No. 2, 87-91 Note Comparison of the Efficacies of Gaseous Ozone and Sodium Hypochlorite in Cleaning Stainless Steel Particles Fouled with Proteins KAZUHIRO TAKAHASHI', KUNIHIKO KOIKE2, AND SATOSHI FUKUZAKI1* Industrial Technology Center of Okayama Prefecture,1 5301 Haga, Okayama 701-1296, and 2Shiga Technology Center, lwatani International Corp., 4-5-1 Katsube, Moriyama, Shiga 524-0041, Japan Received 16 July 2002/Accepted 21 September 2002 The efficacies of gaseous ozone and sodium hypochlorite as an oxidizing agent for cleaning were compared in a laboratory model system using stainless steel particles fouled with pro- teins. Exposure of the protein-fouled stainless steel particles to 0.5% (v/v) gaseous ozone for 30 min enhanced the removal of the various proteins during subsequent alkali cleaning with NaOH solution to the same degree as the NaOH solution containing sodium hypochlorite at 0.2 to 0.4 g/l. The effect of ozone pretreatment on the removal of the proteins depended on the concentration of gaseous ozone. Pretreatment with a highly concentrated gaseous ozone of 20% for 30 min resulted in the almost complete removal of the proteins from stainless steel particles. Key words : Cleaning/Gaseous ozone/Hypochlorite/Protein/Stainless steel. In the food industry, the cleanliness and sterility of 1972). There are many advantages of using ozone as food-processing equipment is one of the most impor- an oxidizing agent in the food industry. Ozone is a tant factors in manufacturing wholesome and safe more powerful oxidant than chlorine and can kill a products. The combined use of detergent and chlo- large number of microorganisms (Graham, 1997; Kim, rine such as sodium hypochlorite has been practiced et al. 1999; Moore, et al. 2000). In addition, ozone can extensively in the dairy industry (Clegg, 1962). The be applied as a gas or in water, and it leaves no resid- main action of hypochlorite is due to the oxidation of ual toxicity after decomposition to oxygen. However, organic substances of soils and microorganisms. few published reports are available on the possible However, the repeated use of chlorinated alkaline de- use of gaseous ozone in the cleaning process. tergent results in the abrasion and corrosion of metal- The aim of this work is to compare the efficacy of lic materials. In addition, chlorination brings health gaseous ozone pretreatment with that of sodium hazards to human beings and wildlife through the pro- hypochlorite in the cleaning of stainless steel particles duction of harmful compounds in the environment fouled with proteins that have different properties, (Richardson et al., 1998). Therefore, alternative e.g., thermal stability, solubility, and structure. cleaning agents to chlorine are being explored for Nonporous stainless steel particles (SUS 304: 2-10 food-processing equipment. One such compound is m) were obtained from The Nilaco Corp. (Tokyo);u ozone (O3) which has been utilized as a sanitizing their specific surface area, as determined by BET agent in European water treatment plants (Gomella, method, was 0.43 m2/g. Crystalline BSA and ƒÀ -lacto- globulin ( ƒÀ -Lg) were purchased from Nacalai *Corresponding author . Tel : +81-82-286-9600, Fax:+ 81-82- Tesque Inc. (Kyoto). Casein and gelatin were pur- 286-9630 chased from Kanto Chemical Co., Inc. (Tokyo) and 88 K. TAKAHASHI ET AL. Wako Pure Chemical Ind. Ltd. (Osaka), respectively. The model protein-fouled stainless steel particles were prepared at 40•Ž by introducing a 50-ml aliquot of a protein solution (3g/l, 10-3 M KNO3) and 10 g of stainless steel particles into a 125-ml glass vial, which was then laid on its side in a water bath at 40 and reciprocally shaken (140 oscillations per min)•Ž for 2 h. The pH values of the protein solutions were adjusted to 5.6 for BSA and gelatin (at the point of zero charge) , and 6.8 for ƒÀ -Lg and casein (pH of milk). After being shaken, the protein-fouled stainless steel particles were collected and washed with 40 ml of 10-3M KNO3 solution by centrifugation (2300 •~g for 1 min). The washed protein-fouled particles were dried at 40•Ž for 16h and stored in a desiccator be- fore use for the cleaning experiments. The amounts of BSA, gelatin, ƒÀ -Lg, and casein adsorbed were 2.7, 1.8, 1.6, and 2.7 mg/m2, respectively. Gaseous ozone of 0.5 to 6.0% (v/v) was gener- ated from pure oxygen (99.999%, v/v) by a silent discharge ozonizer (M001; OHNIT Co. Ltd., Okayama) equipped with an ozone monitor (PG-620; Ebara Jitsugyo Co. Ltd., Tokyo). The above gaseous FIG. 1 . Effects of ozone pretreatment (0.5% for 30 min) ozone was concentrated to 15 and 20% using the and sodium hypochlorite (0.2 g AC//) on the removal of adsorption-desorption technique on silica gel (Koike proteins from stainless steel particles during cleaning with NaOH solutions of different pHs at 40•Ž. (A) BSA, (B) et al., 2000). Prior to cleaning, a 5-g portion of -Lg , (C) casein, (D) gelatin. Batchwise cleaning experi-ƒÀ protein-fouled stainless steel particles was treated ment was conducted at 40•Ž for 2 h with shaking (140 oscil- with gaseous ozone of 0.5 to 20% at room tempera- lations per min). Symbols: A, NaOH alone; O, ozone ture for 30 min. pretreatment; ^, sodium hypochlorite. Batchwise cleaning was conducted by introducing a 1.16-g portion of protein-fouled stainless steel parti- stainless steel particles, and that of the protein in so- cles (ca. 0.5m2) and 5 ml of cleaning solution into a lution were measured with a total organic carbon ana- 25-ml glass vial, which was then placed horizontally in lyzer (TOC-5000; Shimadzu Co., Kyoto) equipped a water bath (40 to 80•Ž) and reciprocally shaken with a solid sample module (SSM-5000; Shimadzu (140 oscillations per min) for 2 h. The pH values of Co., Kyoto). cleaning solutions were adjusted to pH 9.0 to 13.5 Figure 1 shows the effects of gaseous ozone with NaOH (1 M solution). After each cleaning experi- pretreatment (0.5% for 30 min) and sodium ment, the particles bearing the remaining proteins hypochlorite (0.2 g AC/l) on the removal of the pro- were collected by centrifugation (2300 xg for 1 min). teins when used in conjunction with the NaOH solu- To determine the effects of oxidizing agents, protein- tions of different pHs at 40•Ž. In the case of cleaning fouled particles were cleaned at 40•Ž for 2 h with with NaOH solution alone, the removal efficiency was NaOH solutions of pH 9.0 to 13.5 with and without so- markedly higher at pHs above 11 and increased with dium hypochlorite at a final concentration of 0.2 g increasing pH. This indicates that protein removal de- available chlorine (AC) per liter, respectively, as de- pends on the hydroxide ion concentration (Koopal, scribed above. Continuous cleaning was conducted at 1985; Takehara et al., 2001). It was noted that the re- 40•Ž in a stainless steel column (4 mm ƒ³ •~ 50 mm) moval of the proteins occurred markedly at the alka- by feeding 10-3 M KNO3 solution (pH 5.6) for 120 line pH region above the intrinsic dissociation min followed by feeding NaOH solution of pH 12 with constant (pKint) of a side-chain amino group of, for in- or without sodium hypochlorite (0.4g AC/l) for 180 stance, lysine, i.e., 10.8. The use of sodium min at a flow rate of 0.25 ml / min (Urano and hypochlorite and ozone significantly enhanced the re- Fukuzaki, 2001). The alkali eluate was fractionally moval of the proteins. The cleaning effects of ozone collected, and its protein concentration was meas- pretreatment against all the proteins were comparable ured. to those of alkaline hypochlorite solution at 0.2 g AC The amount of protein adsorbed or remaining on /l although small differences in the effects on various CLEANING EFFICACY OF GASEOUS OZONE 89 proteins were observed. The performance of hypochlorite and ozone in removing proteins is asso- ciated with the decomposition of proteins by their strong oxidative power (Merrill et al., 1962; Urano and Fukuzaki, 2001). As a result of decomposition, large fractions of the proteins could be removed even when using a low-pH NaOH solution. It is known that the effects of the combination of NaOH solution and temperature are also to solubilize adsorbed proteins through the chemical reaction be- tween NaOH and proteins, i.e., hydrolysis of proteins (Twomey, 1968). Figure 2 shows the effect of tem- perature on the protein cleaning efficiency by the NaOH solutions of different pHs. All the proteins were removed more efficiently by increasing the tempera- ture from 20 to 80•Ž at pHs especially above 12. Although BSA and p -Lg, which contain sulfhydryl ( SH) groups and are respectively denatured at tem- peratures above 60•Ž and 70•Ž at a neutral pH (De Wit and Swinkels, 1980; Steim, 1965), high tempera- tures under strongly alkaline conditions (pH>12) can enhance the removal of proteins irrespective of the Cleaning time (min) thermal stability of the proteins. As shown in Figs. 1 and 2, in the case of cleaning with a low-pH NaOH so- FIG.3. Time courses for the removal of proteins from stain- lution below 11, the effects of ozone and sodium less steel particles during continuous cleaning with the hypochlorite on the removal of the proteins were NaOH solution of pH 12 alone, NaOH solution (pH 12) com- bined with ozone pretreatment (0.5% for 30 min), or NaOH solution (pH 12) with hypochlorite of 0.4g AC/i.
Load more

Recommended publications
  • 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,
    [Show full text]
  • 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).
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • SODIUM HYPOCHLORITE, AKA “LIQUID CHLORINE” in Other Words, Bleach by the PHTA Recreational Water Quality Committee
    TECH NOTES SODIUM HYPOCHLORITE, AKA “LIQUID CHLORINE” In other words, bleach By the PHTA Recreational Water Quality Committee IN THE SWIMMING pool industry, one gallon of 12.5% sodium hypochlorite a corrosive. As such, a maximum of of the most popularly chosen forms for provides approximately 12.5 ppm of 500 gallons can be stored in a non-fire, sanitizing and superchlorinating water free chlorine per 10,000 gallons of sprinkler-protected room and 1,000 is sodium hypochlorite. Commonly pool water. It takes 10.6 fl. oz of 12.5% gallons in a fire, sprinkler-protected known as “liquid chlorine” or bleach, sodium hypochlorite to get roughly room as maximum exempt quantities. sodium hypochlorite is widely used 1 ppm of free chlorine in 10,000 gallons Quantities beyond this create an “H” in both commercial and residential of pool water. The pH of pool grade Hazardous Occupancy and require swimming pools. Sodium hypochlorite sodium hypochlorite is 13. special fire protection. effectively destroys bacteria and Sodium hypochlorite is Sodium hypochlorite reacts prevents algae in swimming pools. classified as an inorganic sanitizer; in water to create hypochlorous This edition of Tech Notes provides it does not contain cyanuric acid. information on the characteristics, Sodium hypochlorite is a primary effects and proper application of sanitizer because of its ability to SODIUM HYPOCHLORITE: THE sodium hypochlorite. kill microorganisms, oxidize non- living contaminants like ammonia BASIC FACTS WHAT IT IS and swimmers’ waste and provide • Clear yellow liquid with a Sodium hypochlorite (NaOCl), a protective residual in the water. chlorine odor commonly referred to as “liquid Sodium hypochlorite is non-flammable, • A solution containing chlorine” or liquid bleach, is an non-combustible and non-explosive, water, hypochlorite, sodium aqueous solution created by and containers under 1.3 gallons hydroxide and a trace amount mixing chlorine gas in water with aretransported as “Limited Quantities” of sodium chloride concentrations of sodium hydroxide.
    [Show full text]
  • Guidelines for the Use of Sodium Hypochlorite As a Disinfectant for Biological Waste Version 1.0 Prepared By: Animal Research Safety Consultant, Dr
    GUIDELINES FOR USING SODIUM HYPOCHLORITE AS A DISINFECTANT FOR BIOLOGICAL WASTE INTRODUCTION Sodium hypochlorite, commonly known as bleach, is most frequently used as a disinfecting agent. It is a broad-spectrum disinfectant that is effective for the disinfection of viruses, bacteria, fungi, and mycobacterium. However, sodium hypochlorite is NOT effective in the disinfection of bacterial spores and prions. CONCENTRATION & CONTACT TIME The appropriate concentration of sodium hypochlorite for disinfecting general liquid biological waste is 5000 ppm, approximately 0.5%. Household bleach is 5 - 6 % sodium hypochlorite; therefore a 1:10 (v/v) dilution of bleach to liquid biological waste is appropriate. For biological waste containing a high organic load (e.g. blood, proteins, or lipids) the appropriate concentration of sodium hypochlorite is 10000ppm, approximately 1%, therefore a 1:5 (v/v) dilution of bleach to liquid biological waste is appropriate. Minimum Contact time: Surface disinfection - 1 min Liquid waste disinfection - 20 min Important Notes: Discount brands of bleach may have lower concentrations of sodium hypochlorite and "colour safe" bleach contains NO sodium hypochlorite (hydrogen peroxide), these products should NOT be used for the disinfection of biological waste. Sodium hypochlorite is known to be corrosive to metals, therefore, it important to wipe down metal surfaces with water or ethanol after treating them with a bleach solution. STABILITY & STORAGE Bleach should be stored between 2-8°C (50-70°F). According to Clorox, undiluted household bleach has a shelf life of six months to one year from the date of manufacture, after which bleach degrades at a rate of 20% each year until totally degraded to salt and water, and a 1:10 bleach solution has a shelf life of 24 hours.
    [Show full text]
  • Disinfection Evaluation
    DRAFT Disinfection Evaluation Alternatives Analysis January 16, 2019 Prepared for: City of Hastings, MN Prepared by: Ryan Capelle, PE Henry Croll, EIT Revision Description Author Quality Check Independent Review Sign-off Sheet This document entitled Disinfection Evaluation was prepared by Stantec Consulting Ltd. (“Stantec”) for the account of the City of Hastings (the “Client”). Any reliance on this document by any third party is strictly prohibited. The material in it reflects Stantec’s professional judgment in light of the scope, schedule and other limitations stated in the document and in the contract between Stantec and the Client. The opinions in the document are based on conditions and information existing at the time the document was published and do not take into account any subsequent changes. In preparing the document, Stantec did not verify information supplied to it by others. Any use which a third party makes of this document is the responsibility of such third party. Such third party agrees that Stantec shall not be responsible for costs or damages of any kind, if any, suffered by it or any other third party as a result of decisions made or actions taken based on this document. Prepared by (signature) Enter Name Reviewed by (signature) Enter Name Approved by (signature) Enter Name DRAFT DISINFECTION EVALUATION Table of Contents EXECUTIVE SUMMARY .........................................................................................................1.1 1.0 INTRODUCTION .........................................................................................................1.3
    [Show full text]
  • Sodium Hypochlorite
    Right to Know Hazardous Substance Fact Sheet Common Name: SODIUM HYPOCHLORITE Synonyms: Clorox; Liquid Bleach; Sodium Oxychloride CAS Number: 7681-52-9 Chemical Name: Hypochlorous Acid, Sodium Salt RTK Substance Number: 1707 Date: April 2000 Revision: September 2008 DOT Number: UN 1791 Description and Use EMERGENCY RESPONDERS >>>> SEE BACK PAGE Sodium Hypochlorite is a clear, slightly yellow or green liquid Hazard Summary with a strong Chlorine odor. It is usually mixed in water and Hazard Rating NJDOH NFPA used as a household cleaner, a disinfectant, and a bleaching HEALTH 3 - agent. It is also used in water treatment and purification. FLAMMABILITY 0 - REACTIVITY 0 - CORROSIVE POISONOUS GASES ARE PRODUCED IN FIRE Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; Reasons for Citation 4=severe f Sodium Hypochlorite is on the Right to Know Hazardous Substance List because it is cited by DOT, IARC and EPA. f Sodium Hypochlorite can affect you when inhaled. f This chemical is on the Special Health Hazard Substance f Contact can severely irritate and burn the skin and eyes with List. possible eye damage. f Inhaling Sodium Hypochlorite can irritate the nose and throat. f Inhaling Sodium Hypochlorite can irritate the lungs. Higher SEE GLOSSARY ON PAGE 5. exposures may cause a build-up of fluid in the lungs (pulmonary edema), a medical emergency. FIRST AID f Exposure to Sodium Hypochlorite can cause headache, dizziness, nausea and vomiting. Eye Contact f Sodium Hypochlorite is not combustible but is a STRONG f Immediately flush with large amounts of water for at least 30 OXIDIZER which enhances the combustion of other minutes, lifting upper and lower lids.
    [Show full text]
  • Oxychem Sodium Hypochlorite Handbook
    TABLE OF CONTENTS OxyChem Sodium Hypochlorite Handbook Introduction 2 Foreword Properties 3 This handbook outlines recommended methods for handling, storing, and using sodium hypochlorite. It also Concentration Terminology 5 includes information on the manufacture, physical properties, safety considerations and analytical methods for testing sodium Manufacturing 6 hypochlorite. Additional information and contacts can be found at www.oxychem.com Handling and Storage 9 Safety Handling 11 Unloading Tank Trucks 14 Physical Property Data 16 Methods of Analysis 18 Typical Storage Tank Installation 23 Important: The information presented herein, while not guaranteed, was prepared by technical personnel and is true and accurate to the best of our knowledge. NO WARRANTY OF MERCHANTABILITY OR OF FITNESS FOR A PARTICULAR PURPOSE, OR WARRANTY OR GUARANTY OF ANY OTHER KIND, EXPRESS OR IMPLIED, IS MADE REGARDING PERFORMANCE, SAFETY, SUITABILITY, STABILITY OR OTHERWISE. This information is not intended to be all-inclusive as to the manner and conditions of use, handling, storage, disposal and other factors that may involve other or additional legal, environmental, safety or performance considerations, and Occidental Chemical Corporation assumes no liability whatsoever for the use of or reliance upon this information. While our technical personnel will be happy to respond to questions, safe handling and use of the product remains the responsibility of the customer. No suggestions for use are intended as, and nothing herein shall be construed as, a recommendation to infringe any existing patents or to violate any Federal, State, local or foreign laws. INTRODUCTION This handbook provides information Sodium hypochlorite solutions have In 1798, Tennant of England prepared concerning sodium hypochlorite or attained widespread use in bleaching a solution of calcium hypochlorite by bleach, solutions.
    [Show full text]
  • Pamphlet 96 Sodium Hypochlorite Manual
    Pamphlet 96 Sodium Hypochlorite Manual Edition 3 ◗ April 2006 Table of Contents 1 INTRODUCTION............................................................................................................... 1 1.1 SCOPE ...............................................................................................................................1 1.2 CHLORINE INSTITUTE STEWARDSHIP PROGRAM ................................................................... 1 1.3 DISCLAIMER........................................................................................................................ 1 1.4 APPROVAL .......................................................................................................................... 1 1.5 REVISIONS.......................................................................................................................... 1 1.6 REPRODUCTION.................................................................................................................. 1 2 CHEMISTRY AND PHYSICAL PROPERTIES OF SODIUM HYPOCHLORITE .............. 2 2.1 FORMATION REACTION........................................................................................................ 2 2.2 PURITY ...............................................................................................................................2 2.3 STRENGTH OF SOLUTIONS .................................................................................................. 2 2.4 AQUEOUS CHEMISTRY .......................................................................................................
    [Show full text]