METHANESULFONYL FLUORIDE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures.
SYNONYM REFERENCE
USES/FORMS/SOURCES
Methanesulfonyl fluoride is an anticholinesterase compound used as a precursor in the synthesis of perfluoromethane sulfonyl fluoride (PMSF) (Hine et al, 1979). PMSF is then used as a precursor for derivatives used as herbicides and growth regulators, and in the manufacture of disulfone and perfluoromethane sulfonic anhydride industrial catalysts (Hine et al, 1979).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- The following are signs and symptoms from organophosphates in general, which are due to the anticholinesterase activity of this class of compounds. All of these effects may not be documented for methanesulfonyl fluoride, but could potentially occur in individual cases. From available data, it is not apparent that systemic fluoride poisoning can occur following exposure to methanesulfonyl fluoride. If fluoride poisoning is suspected, refer to the FLUORIDE document for more information.
- USES: Methanesulfonyl fluoride is an organophosphate fumigant insecticide; it is not registered as a pesticide in the USA.
- TOXICOLOGY: Organophosphates competitively inhibit pseudocholinesterase and acetylcholinesterase, preventing hydrolysis and inactivation of acetylcholine. Acetylcholine accumulates at nerve junctions, causing malfunction of the sympathetic, parasympathetic, and peripheral nervous systems and some of the CNS. Clinical signs of cholinergic excess can develop.
- EPIDEMIOLOGY: Exposure to organophosphates is common, but serious toxicity is unusual in the US. Common source of severe poisoning in developing countries.
MILD TO MODERATE POISONING: MUSCARINIC EFFECTS: Can include bradycardia, salivation, lacrimation, diaphoresis, vomiting, diarrhea, urination, and miosis. NICOTINIC EFFECTS: Tachycardia, hypertension, mydriasis, and muscle cramps. SEVERE POISONING: MUSCARINIC EFFECTS: Bronchorrhea, bronchospasm, and acute lung injury. NICOTINIC EFFECTS: Muscle fasciculations, weakness, and respiratory failure. CENTRAL EFFECTS: CNS depression, agitation, confusion, delirium, coma, and seizures. Hypotension, ventricular dysrhythmias, metabolic acidosis, pancreatitis, and hyperglycemia can also develop. DELAYED EFFECTS: Intermediate syndrome is characterized by paralysis of respiratory, cranial motor, neck flexor, and proximal limb muscles 1 to 4 days after apparent recovery from cholinergic toxicity, and prior to the development of delayed peripheral neuropathy. Manifestations can include the inability to lift the neck or sit up, ophthalmoparesis, slow eye movements, facial weakness, difficulty swallowing, limb weakness (primarily proximal), areflexia, and respiratory paralysis. Recovery begins 5 to 15 days after onset. Distal sensory-motor polyneuropathy may rarely develop 6 to 21 days following exposure to some organophosphate compounds, however, it has not yet been reported in humans after exposure to methanesulfonyl fluoride. Characterized by burning or tingling followed by weakness beginning in the legs which then spreads proximally. In severe cases, it may result in spasticity or flaccidity. Recovery requires months and may not be complete. CHILDREN: May have different predominant signs and symptoms than adults (more likely CNS depression, stupor, coma, flaccidity, dyspnea, and seizures). Children may also have fewer muscarinic and nicotinic signs of intoxication (i.e., secretions, bradycardia, fasciculations and miosis) as compared to adults. INHALATION EXPOSURE: Organophosphate vapors rapidly produce mucous membrane and upper airway irritation and bronchospasm, followed by systemic muscarinic, nicotinic and central effects if exposed to significant concentrations.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
TOXIC; inhalation, ingestion or contact (skin, eyes) with vapors, dusts or substance may cause severe injury, burns or death. Contact with molten substance may cause severe burns to skin and eyes. Reaction with water or moist air will release toxic, corrosive or flammable gases. Reaction with water may generate much heat that will increase the concentration of fumes in the air. Fire will produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
ACUTE CLINICAL EFFECTS
- Based on its acute oral LD50 of 2 mg/kg in rats (RTECS , 1993), methanesulfonyl fluoride is a HIGHLY TOXIC substance (Morgan, 1989). It can be absorbed following ingestion, inhalation, and parenteral administration (Sax & Lewis, 1989; EPA, 1985). It is not known whether or not this agent can be absorbed through intact skin. No reported cases of human poisoning with this agent were found at the time of this review.
- Methanesulfonyl fluoride is an irreversible inhibitor of acetylcholinesterase in vitro (Krupka, 1975a; Krupka, 1975b; Krupka, 1974; Pavlic, 1987). In this respect, methanesulfonyl fluoride acts similarly to the organophosphate insecticides. Methanesulfonyl fluoride causes acetylcholinesterase inhibition and typical signs of anticholinesterase poisoning in experimental animals (Hine et al, 1979).
- It also inhibits butyrylcholinesterase, but about 20 times more slowly than acetylcholinesterase (Pavlic, 1970) and inhibits trypsinogen in vitro (Morgan & Haas, 1976).
- Effects noted in experimental animals exposed by either the inhalation or intravenous routes included excessive salivation, exudates from the eyes and nose, vomiting, diarrhea, depression, tremors, ataxia, muscle fasciculations, hyperventilation, bronchospasm, and seizures (Hine et al, 1979). Rats exposed by inhalation to low airborne concentrations also had subclinical elevations of blood glucose, serum creatinine, and total bilirubin (Hine et al, 1979).
- The hallmark of anticholinesterase poisoning is inhibition of plasma pseudocholinesterase and erythrocyte acetylcholinesterase (Namba, 1972). Signs and symptoms of anticholinesterase poisoning include nausea, vomiting, abdominal cramps, diarrhea, headache, giddiness, vertigo, weakness, sensation of tightness in the chest (after inhalation exposure), excessive tearing, loss of accommodation, ocular pain, blurring or dimness of vision, miosis, loss of muscle coordination, slurring of speech, fasciculations and twitching of muscles (particularly of tongue and eyelids), generalized profound weakness, mental confusion, disorientation, drowsiness, difficulty in breathing, excessive salivation and respiratory mucus, oronasal frothing, cyanosis, pulmonary rales and rhonchi, hypertension, hypotension, cardiac arrhythmias, random jerking movements, incontinence, seizures, and coma (AH Hall , 1993).
- Death from anticholinesterase poisoning occurs primarily from respiratory arrest arising from failure of the respiratory center, paralysis of respiratory muscles, intense bronchoconstriction, or all three (HSDB , 1993). In severe cases when the patient has been unconscious for some time, brain damage can occur from lack of oxygen (ILO, 1983).
- Some signs and symptoms of acute anticholinesterase poisoning, based upon experience with parathion, can persist for days to months. These include fatigue, ocular symptoms, EEG abnormalities, gastrointestinal complaints, excessive dreams, and intolerance to exposure to organophosphates (ILO, 1983).
- Delayed effects may be most pronounced with highly lipid-soluble organophosphates, such as fenthion, or the phosphorothioates, such as chlorpyrifos. After an initial period of apparent recovery, clinical effects may reoccur for up to several weeks after an acute exposure (Minton & Murray, 1988).
- Some anticholinesterase compounds can induce delayed neurological effects of a motor or combined sensory-motor peripheral polyneuropathy. Sensation of numbness or tingling in the extremities may appear several weeks after acute exposure. It is not clear if all anticholinesterases have this activity (Cherniack, 1986; Wadia et al, 1987).
- In rats exposed by inhalation to an airborne concentration of 2.2 ppm of methanesulfonyl fluoride for 1 hour, only minimal salivation was seen; at a concentration of 5 ppm for the same duration, copious salivation, eye and nose exudates, diarrhea, depression, ataxia, and tremors were observed (Hine et al, 1979).
CHRONIC CLINICAL EFFECTS
- In a study of rats chronically exposed to low doses of methanesulfonyl fluoride by inhalation, fluoride did not accumulate in the blood or liver (Hine et al, 1979). It is not known whether or not systemic fluorosis could occur following exposure to higher doses.
- In general, chronic exposure to anticholinesterases with irreversible inhibition can lead to cumulative depression of cholinesterase levels until a critical lack of activity causes symptoms of anticholinesterase poisoning to appear, in a pattern similar to that of acute poisoning (Coye et al, 1986). The level of chronic exposure which can be tolerated depends on the rate of uptake and degradation of the anticholinesterase compound in the body in relation to its potency in inhibiting acetylcholinesterase, and the rate of the individual's replenishment of acetylcholinesterase activity.
- Only subclinical alterations of blood glucose, serum creatinine, total bilirubin, and depression of acetylcholinesterase were noted in rats exposed by inhalation to 19 or 91 ppb of methanesulfonyl fluoride for 61 exposures, each lasting 7 hours (Hine et al, 1979).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
Universal precautions should be followed by all individuals (i.e., first responders, emergency medical, and emergency department personnel) caring for the patient to avoid contamination. Nitrile gloves are suggested. Avoid direct contact with contaminated clothing, objects or body fluids. Vomiting containing organophosphates should be placed in a closed impervious container for proper disposal.
- DECONTAMINATION OF SPILLS/SUMMARY
A variety of methods have been described for organophosphate spill decontamination, most of which depend on changing the pH to promote hydrolysis to inactive phosphate diester compounds (EPA, 1978). The rate of hydrolysis depends on both the specific organophosphate compound involved and the increase in pH caused by the detoxicant used (EPA, 1978; EPA, 1975). NOTE: Do NOT use a MIXTURE of BLEACH and ALKALI for DECONTAMINATING ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). This can cause release of toxic acetyl chloride, acetylene, and phosgene gas. Spills of acephate organophosphates should be decontaminated by absorption and scrubbing with concentrated detergent (Ford JE, 1989).
Treatment of the spilled material with alkaline substances such as sodium carbonate (soda ash), sodium bicarbonate (baking soda), calcium hydroxide (slaked or hydrated lime), calcium hydroxide (lime or lime water, when in dilute solutions), and calcium carbonate (limestone) may be used for detoxification (EPA, 1975a). Chlorine-active compounds such as sodium hypochlorite (household bleach) or calcium hypochlorite (bleaching powder, chlorinated lime) may also be used to detoxify organophosphate spills (EPA, 1975a). While ammonia compounds have also been suggested as alternate detoxicants for organophosphate spills, UNDER NO CIRCUMSTANCES SHOULD AMMONIA EVER BE COMBINED WITH A CHLORINE-ACTIVE COMPOUND (BLEACH) AS HIGHLY IRRITATING CHLORAMINE GAS MAY BE EVOLVED.
- SMALL SPILL DECONTAMINATION
Three cups of Arm & Hammer washing soda (sodium carbonate) or Arm & Hammer baking soda (sodium bicarbonate) may be combined with one-half cup of household bleach and added to a plastic bucket of water. The washing soda is more alkaline and may be more efficacious, if available. Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Spilled liquid may first be adsorbed with soil, sweeping compound, sawdust, or dry sand and then both the adsorbed material and the floor decontaminated with one of the above solutions (EPA, 1975a). NOTE: Do NOT use a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get fire-fighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; re-absorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent. Call the National Pesticide Telecommunications Network for further assistance at 1-800-858-7378 or on the web at http://nptn.orst.edu.
- LARGE SPILL DECONTAMINATION
Sprinkle or spray the area with a mixture of one gallon of sodium hypochlorite (bleach) mixed with one gallon of water. Then spread calcium hydroxide (hydrated or slaked lime) liberally over the area and allow to stand for at least one hour (Pesticide User's Guide, 1976). Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Other decontamination methods may be recommended by manufacturers of specific agents. Check containers, labels, or product literature for possible instructions regarding spill decontamination. NOTE: Do NOT USE a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get fire-fighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; re-absorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent.
FURTHER CONTACT INFORMATION For further information contact the National Pesticide Telecommunications Network at 1-800-858-7378 or contact on the web at http://nptn.orst.edu. Disposal of large quantities or contamination of large areas may be regulated by various governmental agencies and reporting may be required. For small pesticide spills or for further information call the pesticide manufacturer or the National Pesticide Information Center (NPIC) at 1-800-858-7378. The National Response Center (NRC) is the federal point of contact for reporting of spills and can be reached at 1-800-424-8802. For those without 800 access, contact 202-267-2675. CHEMTREC can provide technical and hazardous materials information and can be reached at 1-800-424-9300 in the US; or 703-527-3887 outside the US.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance; give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
ORAL EXPOSURE DERMAL EXPOSURE EYE EXPOSURE INHALATION EXPOSURE PERSONNEL PROTECTION Universal precautions should be followed by all individuals (i.e., first responders, emergency medical, and emergency department personnel) caring for the patient to avoid contamination. Nitrile gloves are suggested. Avoid direct contact with contaminated clothing, objects or body fluids. Vomiting containing organophosphates should be placed in a closed impervious container for proper disposal.
DECONTAMINATION OF SPILLS/SUMMARY A variety of methods have been described for organophosphate spill decontamination, most of which depend on changing the pH to promote hydrolysis to inactive phosphate diester compounds (EPA, 1978). The rate of hydrolysis depends on both the specific organophosphate compound involved and the increase in pH caused by the detoxicant used (EPA, 1978; EPA, 1975). NOTE: Do NOT use a MIXTURE of BLEACH and ALKALI for DECONTAMINATING ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). This can cause release of toxic acetyl chloride, acetylene, and phosgene gas. Spills of acephate organophosphates should be decontaminated by absorption and scrubbing with concentrated detergent (Ford JE, 1989).
Treatment of the spilled material with alkaline substances such as sodium carbonate (soda ash), sodium bicarbonate (baking soda), calcium hydroxide (slaked or hydrated lime), calcium hydroxide (lime or lime water, when in dilute solutions), and calcium carbonate (limestone) may be used for detoxification (EPA, 1975a). Chlorine-active compounds such as sodium hypochlorite (household bleach) or calcium hypochlorite (bleaching powder, chlorinated lime) may also be used to detoxify organophosphate spills (EPA, 1975a). While ammonia compounds have also been suggested as alternate detoxicants for organophosphate spills, UNDER NO CIRCUMSTANCES SHOULD AMMONIA EVER BE COMBINED WITH A CHLORINE-ACTIVE COMPOUND (BLEACH) AS HIGHLY IRRITATING CHLORAMINE GAS MAY BE EVOLVED.
SMALL SPILL DECONTAMINATION Three cups of Arm & Hammer washing soda (sodium carbonate) or Arm & Hammer baking soda (sodium bicarbonate) may be combined with one-half cup of household bleach and added to a plastic bucket of water. The washing soda is more alkaline and may be more efficacious, if available. Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Spilled liquid may first be adsorbed with soil, sweeping compound, sawdust, or dry sand and then both the adsorbed material and the floor decontaminated with one of the above solutions (EPA, 1975a). NOTE: Do NOT use a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get fire-fighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; re-absorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent. Call the National Pesticide Telecommunications Network for further assistance at 1-800-858-7378 or on the web at http://nptn.orst.edu.
LARGE SPILL DECONTAMINATION Sprinkle or spray the area with a mixture of one gallon of sodium hypochlorite (bleach) mixed with one gallon of water. Then spread calcium hydroxide (hydrated or slaked lime) liberally over the area and allow to stand for at least one hour (Pesticide User's Guide, 1976). Wear rubber gloves, and use a respirator certified effective against toxic vapors. Several washes may be required for decontamination (EPA, 1978). Other decontamination methods may be recommended by manufacturers of specific agents. Check containers, labels, or product literature for possible instructions regarding spill decontamination. NOTE: Do NOT USE a COMBINATION of BLEACH and ALKALI to DECONTAMINATE ACEPHATE or ACETYL ORGANOPHOSPHATE COMPOUNDS such as ORTHENE(R). Spills involving acephate organophosphates should be decontaminated by the following procedure - Isolate and ventilate the area; keep sources of fire away; wear rubber or neoprene gloves and overshoes; get fire-fighting equipment ready; contain any liquid spill around the edge and absorb with Zorb-All(R) or similar material; dispose of absorbed or dry material in disposable containers; scrub the spilled area with concentrated detergent such as TIDE(R), ALL(R) or similar product; re-absorb scrubbing liquid and dispose as above; dispose of cleaning materials and contaminated clothing; wash gloves, overshoes and shovel with concentrated detergent.
FURTHER CONTACT INFORMATION For further information contact the National Pesticide Telecommunications Network at 1-800-858-7378 or contact on the web at http://nptn.orst.edu. Disposal of large quantities or contamination of large areas may be regulated by various governmental agencies and reporting may be required. For small pesticide spills or for further information call the pesticide manufacturer or the National Pesticide Information Center (NPIC) at 1-800-858-7378. The National Response Center (NRC) is the federal point of contact for reporting of spills and can be reached at 1-800-424-8802. For those without 800 access, contact 202-267-2675. CHEMTREC can provide technical and hazardous materials information and can be reached at 1-800-424-9300 in the US; or 703-527-3887 outside the US.
ANTIDOTES
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
In rats exposed by inhalation to a concentration of 2.2 parts per million for 1 hour, only minimal salivation was seen; at 5 parts per million for the same duration, copious salivation, eye and nose exudates, diarrhea, depression, ataxia, and tremors were observed (Hine et al, 1979). Only subclinical alterations of blood glucose, serum creatinine, total bilirubin, and depression of acetylcholinesterase were noted in rats exposed by inhalation to 19 or 91 parts per billion of methanesulfonyl fluoride for 61 exposures, each lasting 7 hours (Hine et al, 1979).
- Carcinogenicity Ratings for CAS558-25-8 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed MAK (DFG, 2002): Not Listed NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS558-25-8 (U.S. Environmental Protection Agency, 2011):
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS558-25-8 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS558-25-8 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS558-25-8 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS558-25-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS558-25-8 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS558-25-8 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS558-25-8 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS558-25-8 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS558-25-8 (U.S. Environmental Protection Agency, 2010):
Listed as: Methanesulfonyl Fluoride Reportable Quantity, in pounds: 1000 Threshold Planning Quantity, in pounds: Note(s): Not Listed
- EPA SARA Title III, Community Right-to-Know for CAS558-25-8 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS558-25-8 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS558-25-8 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions (49 CFR 172.101, 2005):
- ICAO International Shipping Name (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS558-25-8 (NFPA, 2002):
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
RESPIRATORY PROTECTION
- Respiratory protection is recommended for safe handling and use of methanesulfonyl fluoride (EPA, 1985).
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 558-25-8.
-PHYSICAL HAZARDS
FIRE HAZARD
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures. POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004) Combustible material: may burn but does not ignite readily. Substance will react with water (some violently) releasing flammable, toxic or corrosive gases and runoff. When heated, vapors may form explosive mixtures with air: indoors, outdoors and sewers explosion hazards. Most vapors are heavier than air. They will spread along ground and collect in low or confined areas (sewers, basements, tanks). Vapors may travel to source of ignition and flash back. Contact with metals may evolve flammable hydrogen gas. Containers may explode when heated or if contaminated with water.
Methanesulfonyl fluoride releases toxic and irritating fumes of fluorides and oxides of sulfur when heated to decomposition (Sax & Lewis, 1989).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS558-25-8 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
Water spray, fog or alcohol-resistant foam. FOR CHLOROSILANES, DO NOT USE WATER; use AFFF alcohol-resistant medium expansion foam. Move containers from fire area if you can do it without risk. Use water spray or for; do not use straight streams.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire.
- NFPA Extinguishing Methods for CAS558-25-8 (NFPA, 2002):
DUST/VAPOR HAZARD
- Methanesulfonyl fluoride releases toxic and irritating fumes of fluorides and oxides of sulfur when heated to decomposition (Sax & Lewis, 1989).
REACTIVITY HAZARD
- Methanesulfonyl fluoride releases toxic and irritating fumes of fluorides and oxides of sulfur when heated to decomposition (Lewis, 1992).
EVACUATION PROCEDURES
- Initial Isolation and Protective Action Distances (ERG, 2004)
Data presented from the Emergency Response Guidebook Table of Initial Isolation and Protective Action Distances are for use when a spill has occurred and there is no fire. If there is a fire, or if a fire is involved, evacuation information presented under FIRE - PUBLIC SAFETY EVACUATION DISTANCES should be used. Generally, a small spill is one that involves a single, small package such as a drum containing up to approximately 200 liters, a small cylinder, or a small leak from a large package. A large spill is one that involves a spill from a large package, or multiple spills from many small packages. Suggested distances to protect from vapors of toxic-by-inhalation and/or water-reactive materials during the first 30 minutes following the spill. - SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and 25 meters (75 feet) for solids in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
- PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate enclosed areas.
- AIHA ERPG Values for CAS558-25-8 (AIHA, 2006):
- DOE TEEL Values for CAS558-25-8 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Methanesulfonyl fluoride (Methanesulfonyl fluoride) TEEL-0 (units = ppm): 0.6 TEEL-1 (units = ppm): 2 TEEL-2 (units = ppm): 3.49 TEEL-3 (units = ppm): 3.49 Definitions: TEEL-0: The threshold concentration below which most people will experience no adverse health effects. TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure. TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape. TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.
- AEGL Values for CAS558-25-8 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; United States Environmental Protection Agency Office of Pollution Prevention and Toxics, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS558-25-8 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). All equipment used when handling the product must be grounded. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. A vapor suppressing foam may be used to reduce vapors. FOR CHLOROSILANES, use AFFF alcohol-resistant medium expansion foam to reduce vapors. DO NOT GET WATER on spilled substance or inside containers. Use water spray to reduce vapors or divert vapor cloud drift. Avoid allowing water runoff to contact spilled material. Prevent entry into waterways, sewers, basements or confined areas.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 156 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
There was no specific information on the disposal of methanesulfonyl fluoride in available references at the time of this review. Avoid inhalation of methanesulfonyl fluoride. Wear proper respiratory protection (EPA, 1985).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- There was no information on the pollution hazard of methanesulfonyl fluoride in available references at the time of this review.
ENVIRONMENTAL FATE AND KINETICS
ENVIRONMENTAL TOXICITY
- There was no information on the environmental toxicity of methanesulfonyl fluoride in available references at the time of this review.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
- 98.10 (RTECS, 1996; (Hine et al, 1979; EPA, 1985)
DESCRIPTION/PHYSICAL STATE
- Methanesulfonyl fluoride is a clear, colorless liquid (Hine et al, 1979).
PH
VAPOR PRESSURE
- 19.2 mmHg (at 21 degrees C) (Hine et al, 1979)
BOILING POINT
- 126 degrees C (Hine et al, 1979)
SOLUBILITY
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