DICHLOROFLUOROMETHANE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
ALGOFRENE TYPE 5 ARCTON 7 CFC-21 DICHLOROFLUOROMETHANE DICHLOROMONOFLUOROMETHANE DWUCHLOROFLUOROMETAN (Polish) F 21 F-21 FC 21 FC-21 FLUOROCARBON 21 FLUORODICHLOROMETHANE FREON 21 FREON F 21 GENETRON 21 HALOCARBON 21 HALON 112 HCFC 21 HFC-21 METHANE, DICHLOROFLUORO- MONOFLUORODICHLOROMETHANE RACON 21 R21 R 21 (refrigerant) R-21 REFRIGERANT 21 REFRIGERANT R21
IDENTIFIERS
SYNONYM REFERENCE
- (Ashford, 1994; Bingham et al, 2001; CHRIS , 2002; HSDB , 2002; RTECS , 2002)
USES/FORMS/SOURCES
Dichlorofluoromethane is used as a solvent, a refrigerant, an aerosol propellant, a fire-extinguishing agent, and a heat-exchange medium. It is one of the group of halogenated chlorofluorocarbons (CFCs) being phased out of production under the 1987 Montreal Protocol (ACGIH, 1991; Bingham et al, 2001; Hathaway et al, 1996; ITI, 1995; HSDB , 2002).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- LOW CONCENTRATION - Inhalations such as those caused by leaking air conditioners or refrigerators usually result in transient eye, nose, and throat irritation. Palpitations, light-headedness, and headaches are also seen.
- HIGH CONCENTRATION - Inhalation associated with deliberate abuse, or spills or industrial use occurring in poorly ventilated areas has been associated with ventricular arrhythmias, pulmonary edema and sudden death.
- Aerosol propellant abuse of chlorofluorocarbons can result in "sudden sniffing death". Myocardial sensitization to endogenous catecholamines producing refractory ventricular arrhythmias is the most likely mechanism. Some individuals may be susceptible to the arrhythmogenic effects at relatively low concentrations of dichlorofluoromethane.
- Dichlorofluoromethane can act as a simple asphyxiant by displacing oxygen from the breathing atmosphere. Signs and symptoms of exposure may include air hunger, giddiness, light-headedness, disorientation, narcosis, tremor, arrhythmias, hypotension, nausea, and vomiting.
- Inhalation of evolved chloride and fluoride fumes in a fire could cause eye, nose, and throat irritation; chemical pneumonitis; or noncardiogenic pulmonary edema.
- Direct contact with the liquified material or escaping compressed gas may cause frostbite injury.
- In experimental animals, repeated or prolonged single exposures have caused liver injury. Convulsive movements have been noted in the animals prior to death. Mice exposed to 100,000 ppm (10 percent) had a lowering of the myocardial threshold to the arrhythmogenic effects of injected epinephrine.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004)
Vapors may cause dizziness or asphyxiation without warning. Vapors from liquefied gas are initially heavier than air and spread along ground. Contact with gas or liquefied gas may cause burns, severe injury and/or frostbite. Fire may produce irritating, corrosive and/or toxic gases.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with liquefied gas, thaw frosted parts with lukewarm water. Keep victim warm and quiet. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
FIRST AID EYE EXPOSURE - If eye tissue is frozen, seek medical attention immediately; if tissue is not frozen, immediately and thoroughly flush the eyes with large amounts of water for at least 15 minutes, occasionally lifting the lower and upper eyelids. If irritation, pain, swelling, lacrimation, or photophobia persist, get medical attention as soon as possible. Primary eye protection (spectacles or goggles), as defined by the Occupational Safety and Health Administration (OSHA), should be used when working with this chemical. Face shields should only be worn over primary eye protection. Contact lens use is not recommended when working with this chemical. If contact lenses are worn, then appropriate eye and face protection devices must be used. OSHA emphasizes that dusty and/or chemical environments may represent an additional hazard to contact lens wearers.
DERMAL EXPOSURE - If frostbite has occurred, seek medical attention immediately; do NOT rub the affected areas or flush them with water. In order to prevent further tissue damage, do NOT attempt to remove frozen clothing from frostbitten areas. If frostbite has NOT occurred, immediately and thoroughly wash contaminated skin with soap and water. INHALATION EXPOSURE - Move the exposed person to fresh air at once. If breathing has stopped, perform artificial respiration. Keep the affected person warm and at rest. Get medical attention as soon as possible. TARGET ORGANS - Respiratory system and cardiovascular system (National Institute for Occupational Safety and Health, 2007; OSHA, 2000).
INHALATION EXPOSURE - INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm. If bronchospasm and wheezing occur, consider treatment with inhaled sympathomimetic agents. ACUTE LUNG INJURY: Maintain ventilation and oxygenation and evaluate with frequent arterial blood gases and/or pulse oximetry monitoring. Early use of PEEP and mechanical ventilation may be needed. SEIZURES: Administer a benzodiazepine; DIAZEPAM (ADULT: 5 to 10 mg IV initially; repeat every 5 to 20 minutes as needed. CHILD: 0.1 to 0.5 mg/kg IV over 2 to 5 minutes; up to a maximum of 10 mg/dose. May repeat dose every 5 to 10 minutes as needed) or LORAZEPAM (ADULT: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist. CHILD: 0.05 to 0.1 mg/kg IV over 2 to 5 minutes, up to a maximum of 4 mg/dose; may repeat in 5 to 15 minutes as needed, if seizures continue). Consider phenobarbital or propofol if seizures recur after diazepam 30 mg (adults) or 10 mg (children greater than 5 years). Monitor for hypotension, dysrhythmias, respiratory depression, and need for endotracheal intubation. Evaluate for hypoglycemia, electrolyte disturbances, and hypoxia.
Cardiac monitoring may be advisable in cases of significant exposure. Whenever possible, the administration of epinephrine should be avoided in patients with chlorofluorocarbon inhalation exposure. If epinephrine is required for the treatment of life-threatening conditions, it should be administered in the lowest possible dose, careful and continuous cardiac monitoring should be done, and resuscitation equipment and supplies should be readily available.
DERMAL EXPOSURE - DECONTAMINATION: Remove contaminated clothing and jewelry and place them in plastic bags. Wash exposed areas with soap and water for 10 to 15 minutes with gentle sponging to avoid skin breakdown. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999). If frostbite has occurred, DO NOT rub affected areas, DO NOT flush affected areas with water, or attempt to remove clothing. PREHOSPITAL Rewarming of a localized area should only be considered if the risk of refreezing is unlikely. Avoid rubbing the frozen area which may cause further damage to the area (Grieve et al, 2011; Hallam et al, 2010).
REWARMING Do not institute rewarming unless complete rewarming can be assured; refreezing thawed tissue increases tissue damage. Place affected area in a water bath with a temperature of 40 to 42 degrees Celsius for 15 to 30 minutes until thawing is complete. The bath should be large enough to permit complete immersion of the injured part, avoiding contact with the sides of the bath. A whirlpool bath would be ideal. Some authors suggest a mild antibacterial (ie, chlorhexidine, hexachlorophene or povidone-iodine) be added to the bath water. Tissues should be thoroughly rewarmed and pliable; the skin will appear a red-purple color (Grieve et al, 2011; Hallam et al, 2010; Murphy et al, 2000). Correct systemic hypothermia which can cause cold diuresis due to suppression of antidiuretic hormone; consider IV fluids (Grieve et al, 2011). Rewarming may be associated with increasing acute pain, requiring narcotic analgesics. For severe frostbite, clinical trials have shown that pentoxifylline, a phosphodiesterase inhibitor, can enhance tissue viability by increasing blood flow and reducing platelet activity (Hallam et al, 2010).
WOUND CARE Digits should be separated by sterile absorbent cotton; no constrictive dressings should be used. Protective dressings should be changed twice per day. Perform twice daily hydrotherapy for 30 to 45 minutes in warm water at 40 degrees Celsius. This helps debride devitalized tissue and maintain range of motion. Keep the area warm and dry between treatments (Hallam et al, 2010; Murphy et al, 2000). The injured extremities should be elevated and should not be allowed to bear weight. In patients at risk for infection of necrotic tissue, prophylactic antibiotics and tetanus toxoid have been recommended by some authors (Hallam et al, 2010; Murphy et al, 2000). Non-tense clear blisters should be left intact due to the risk of infection; tense or hemorrhagic blisters may be carefully aspirated in a setting where aseptic technique is provided (Hallam et al, 2010). Further surgical debridement should be delayed until mummification demarcation has occurred (60 to 90 days). Spontaneous amputation may occur. Analgesics may be required during the rewarming phase; however, patients with severe pain should be evaluated for vasospasm. IMAGING: Arteriography and noninvasive vascular techniques (e.g., plain radiography, laser Doppler studies, digital plethysmography, infrared thermography, isotope scanning), have been useful in evaluating the extent of vasospasm after thawing and assessing whether debridement is needed (Hallam et al, 2010). In cases of severe frostbite, Technetium 99 (triple phase scanning) and MRI angiography have been shown to be the most useful to assess injury and determine the extent or need for surgical debridement (Hallam et al, 2010). TOPICAL THERAPY: Topical aloe vera may decrease tissue destruction and should be applied every 6 hours (Murphy et al, 2000). IBUPROFEN THERAPY: Ibuprofen, a thromboxane inhibitor, may help limit inflammatory damage and reduce tissue loss (Grieve et al, 2011; Murphy et al, 2000). DOSE: 400 mg orally every 12 hours is recommended (Hallam et al, 2010). THROMBOLYTIC THERAPY: Thrombolysis (intra-arterial or intravenous thrombolytic agents) may be beneficial in those patients at risk to lose a digit or a limb, if done within the first 24 hours of exposure. The use of tissue plasminogen activator (t-PA) to clear microvascular thromboses can restore arterial blood flow, but should be accompanied by close monitoring including angiography or technetium scanning to evaluate the injury and to evaluate the effects of t-PA administration. Potential risk of the procedure includes significant tissue edema that can lead to a rise in interstitial pressures resulting in compartment syndrome (Grieve et al, 2011). CONTROVERSIAL: Adjunct pharmacological agents (ie, heparin, vasodilators, prostacyclins, prostaglandin synthetase inhibitors, dextran) are controversial and not routinely recommended. The role of hyperbaric oxygen therapy, sympathectomy remains unclear (Grieve et al, 2011). CHRONIC PAIN: Vasomotor dysfunction can produce chronic pain. Amitriptyline has been used in some patients; some patients may need a referral for pain management. Inability to tolerate the cold (in the affected area) has been observed following a single episode of frostbite (Hallam et al, 2010). MORBIDITIES: Frostbite can produce localized osteoporosis and possible bone loss following a severe case. These events may take a year or more to develop. Children may be at greater risk to develop more severe events (ie, early arthritis) (Hallam et al, 2010).
EYE EXPOSURE - DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility. If contact with escaping gas may have caused frostbite of the eyes, DO NOT flush with water; early ophthalmologic consultation should be obtained.
ORAL EXPOSURE -
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
Fatalities were seen in guinea pigs exposed to 400,000 ppm (40 percent) dichlorofluoromethane in 18 percent oxygen. Fatalities were also seen with exposure to 102,000 ppm (10.2 percent) (Hathaway et al, 1996).
MAXIMUM TOLERATED EXPOSURE
Tremors, incoordination, and irregular breathing were seen in animals exposed to 52,000 ppm (5.2 percent) (Hathaway et al, 1996). Rats exposed for 90 days to 1000 and 5000 ppm suffered hair loss, extensive liver injury, and excessive mortality (Hathaway et al, 1996). Mice exposed to 100,000 ppm (10 percent) had induced arrhythmias and a lowering of the myocardial threshold to the arrhythmogenic effects of injected epinephrine (Hathaway et al, 1996). Adverse reproductive effects were seen in female rats exposed to 10,000 ppm (1 percent) on days 6 through 15 of gestation (Hathaway et al, 1996).
- Carcinogenicity Ratings for CAS75-43-4 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Dichlorofluoromethane 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 ; Listed as: Dichloromonofluoromethane 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 CAS75-43-4 (U.S. Environmental Protection Agency, 2011):
CALCULATIONS
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS75-43-4 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
- AIHA WEEL Values for CAS75-43-4 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS75-43-4 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS75-43-4 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS75-43-4 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS75-43-4 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS75-43-4 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS75-43-4 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS75-43-4 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS75-43-4 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Dichlorofluoromethane (HCFC-21) Effective Date for Reporting Under 40 CFR 372.30: 1/1/95 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS75-43-4 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS75-43-4 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1029 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1029 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS75-43-4 (NFPA, 2002):
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (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 will only provide limited protection.
- As this compound can cause frostbite to skin, appropriate protective clothing should be worn. This includes rubber gloves, a self-contained breathing apparatus, safety goggles, and safety shoes. If clothing becomes wet or contaminated, it should be removed immediately (CHRIS , 2002; ILO , 1998; ITI, 1995; NIOSH , 2002; Sittig, 1991).
- "Quick drench facilities and/or eyewash fountains should be provided within the immediate work area for emergency use where there is any possibility of exposure to liquids that are extremely cold or rapidly evaporating" (NIOSH , 2002).
EYE/FACE PROTECTION
- Eye protection should be worn (NIOSH , 2002).
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
- Dichlorofluoromethane may cause asphyxiation by the displacement of air (AAR, 2002).
- "Individual breathing devices with independent air supply will minimize risk of inhalation. Lifelines should be worn when entering tanks or other confined spaces" (HSDB , 2002).
- 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 75-43-4.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004) Some may burn, but none ignite readily. Containers may explode when heated. Ruptured cylinders may rocket.
"Nonflammable. Container may explode in heat of fire. Move container from fire area if you can do it w/out risk. Stay away from ends of tanks. Cool containers that are exposed to flames with water from the side until well after fire is out. Withdraw immediately in case of rising sound from venting safety device or any discoloration of tanks due to fire" (CHRIS , 2002). If dichlorofluoromethane is involved in a fire, corrosive and toxic fumes of chlorine, fluorine, hydrogen chloride, hydrogen fluoride, and phosgene may be released (ACGIH, 1991; ILO , 1998; Lewis, 2000; CHRIS , 2002). If exposure to prolonged heat of fire is allowed, the container may rupture violently and rocket (AAR, 2000).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS75-43-4 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Damaged cylinders should be handled only by specialists.
- TANK FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Cool containers with flooding quantities of water until well after fire is out. Do not direct water at source of leak or safety devices; icing may occur. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. Some of these materials, if spilled, may evaporate leaving a flammable residue.
- NFPA Extinguishing Methods for CAS75-43-4 (NFPA, 2002):
- As dichlorofluoromethane itself is weakly flammable or nonflammable, fires involving this compound should be extinguished using an agent suitable for the surrounding fire type. To avoid container heating and subsequent chemical decomposition and release of corrosive and toxic fumes, affected containers can be cooled by flooding with quantities of water applied from a maximal distance (AAR, 2000; ILO , 1998).
If heated to decomposition, dichlorofluoromethane will produce highly toxic and corrosive fumes, such as hydrogen chloride, hydrogen fluoride, phosgene, chlorine, and fluorine (ACGIH, 1991; ILO , 1998; Lewis, 2000; CHRIS , 2002). "All fluorocarbons will undergo thermal decomposition when exposed to flame or red-hot metal. Decomposition products of the chlorofluorocarbons will include hydrofluoric and hydrochloric acid along with smaller amounts of phosgene and carbonyl fluoride. The last compound is very unstable to hydrolysis and quickly changes to hydrofluoric acid & carbon dioxide in the presence of moisture" (HSDB , 2002).
EXPLOSION HAZARD
- Containers may explode if exposed to the heat of a fire (CHRIS , 2002).
During a fire, stay away from the ends of tanks (CHRIS , 2002). If a rising sound is heard from a venting safety device or if a tank is discolored due to fire, withdraw immediately (CHRIS , 2002).
- Containers of dichlorofluoromethane that are exposed to prolonged heat or fire may rupture violently and rocket (AAR, 2000).
DUST/VAPOR HAZARD
- Decomposition of dichlorofluoromethane may release toxic and corrosive fumes, such as hydrogen chloride, hydrogen fluoride, and phosgene. Heating of dichlorofluoromethane will generate these decomposition products, as well as toxic fumes of chlorine and fluorine (ACGIH, 1991; Lewis, 2000).
- Highly toxic fumes (chlorine, fluorine) are generated when dichlorofluoromethane reacts with acids or acid fumes (ILO , 1998).
- Dichlorofluoromethane can cause asphyxia by displacement of oxygen from the breathing atmosphere. Because its vapors are four to five times heavier than air, it can accumulate in low-lying areas (CHRIS , 2002; Proctor et al, 1988).
- During a spill or leak of dichlorofluoromethane, use of a water spray will reduce vapors and divert drifting of gaseous vapors. Entry into basements or confined areas should be prevented (HSDB , 2002).
REACTIVITY HAZARD
- Dichlorofluoromethane is incompatible and can react violently with chemically active metals such as calcium, sodium, potassium, powdered aluminum, magnesium, and zinc. It also reacts with acid and acid fumes to produce highly toxic fumes of chlorine and fluorine (ACGIH, 1991; NIOSH , 2002; Lewis, 2000; ILO , 1998; HSDB , 2002).
- Some forms or plastics, rubber, and coatings will be attacked by this chemical (ACGIH, 1991; ILO , 1998).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- LARGE SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (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 126 (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 for at least 100 meters (330 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Many gases are heavier than air and will spread along ground and collect in low or confined areas (sewers, basements, tanks). Keep out of low areas. Ventilate closed spaces before entering.
- AIHA ERPG Values for CAS75-43-4 (AIHA, 2006):
- DOE TEEL Values for CAS75-43-4 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Dichlorofluoromethane (Freon 21, CFC 21) TEEL-0 (units = ppm): 10 TEEL-1 (units = ppm): 1,500 TEEL-2 (units = ppm): 5,000 TEEL-3 (units = ppm): 5,000 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 CAS75-43-4 (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; 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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 CAS75-43-4 (National Institute for Occupational Safety and Health, 2007):
IDLH: 5000 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (ERG, 2004) Do not touch or walk through spilled material. Stop leak if you can do it without risk. Do not direct water at spill or source of leak. Use water spray to reduce vapors or divert vapor cloud drift. Avoid allowing water runoff to contact spilled material. If possible, turn leaking containers so that gas escapes rather than liquid. Prevent entry into waterways, sewers, basements or confined areas. Allow substance to evaporate. Ventilate the area.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 126 (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 will only provide limited protection.
Incineration is a recommended disposal method for this compound. However, the formation of phosgene can be prevented by assuring complete combustion and use of engineering controls such as an acid scrubber to remove halo acids generated during combustion (Sittig, 1991). As dichlorofluoromethane has the potential to decompose ozone in the stratosphere, this material should be released to that atmosphere as a last resort only (Sittig, 1991). "If Refrigerant 21 is spilled or leaked, the following steps should be taken: 1. Ventilate area of spill or leak. 2. If the gas is leaking, stop the flow. 3. If the liquid is spilled or leaked, allow to vaporize" (HSDB , 2002). Removal Method: The destruction of chlorofluoromethanes (CFCs) was studied in a turbulent jet-stirred burner. The output gases were absorbed in water and decane. The destruction of CFCs was 99.995% or better as determined by gas chromatography using electron capture detection (Pederson & Kallman, 1992).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- The production, storage, transport, and use of dichlorofluoromethane may result in its release to the environment. It has also been reported to exist naturally in emissions from volcanoes (Howard, 1993).
- Its use as a refrigerant, solvent, or aerosol propellant generally results in dichlorofluoromethane's eventual loss to the atmosphere, unless it is captured and recycled (HSDB, 2004).
ENVIRONMENTAL FATE AND KINETICS
With a vapor pressure of 1.36 x 10(3) mm Hg (at 25 degrees C), dichlorofluoromethane will exist solely in the gas phase in the ambient atmosphere. Its physiochemical properties suggest it will mix rapidly within the lower region of the atmosphere. Atmospheric removal of dichlorofluoromethane primarily occurs by reaction with photochemically-produced hydroxyl radicals by H-atom abstraction. The rate constant for this reaction was found to vary between 2.6 to 3.54 x 10(-14) cm(3)/molecule-sec (within the range of 20 to 25 degrees C). An atmospheric half-life of approximately 1.5 years was determined assuming a rate constant of 3 x 10(-14) cm(3)/molecule-sec and using an average tropospheric hydroxyl radical concentration of 5 x 10(5). The half-life in the troposphere was estimated to be from 1.5 to 2 years (HSDB, 2004; Bingham et al, 2001; Howard, 1993). A two-dimensional, tropospheric model that considered both vertical and latitudinal transport as well as reaction with atmospheric species was used to estimate a 2 year half-life in the troposphere. As a result of its long half-life, dichlorofluoromethane released to the atmosphere will accumulate and disperse throughout the troposphere across the globe. About 5% of the atmospheric dichlorofluoromethane is predicted to diffuse to the stratosphere where it will be destroyed as a result of photodissociation and reaction with hydroxyl radicals and O(1D) atoms. Photodissociation produces free chlorine atoms (free radicals) which catalyze destruction of the ozone layer (Howard, 1993; HSDB, 2004).
Dichlorofluoromethane's removal from the atmosphere also occurs by wet deposition due to its high water solubility. It will eventually be re-released back into the atmosphere by volatilization from water (Howard, 1993).
SURFACE WATER Dichlorofluoromethane has a very low rate of hydrolysis in water. Its lack of a suitable chromophoric group precludes direct photolysis in water. Removal from water occurs predominantly be by volatilization. Based on its estimated organic carbon partition coefficient (Koc) value of 35 [determined from a measured log octanol water partition coefficient (Kow) of 1.55 and a regression-derived equation], dichlorofluoromethane will not adsorb appreciably to sediment or suspended solids in water. The estimated low bioconcentration factor (BCF) value suggests bioconcentration of the compound in aquatic organisms will not be important (Howard, 1993; HSDB, 2004). Dichlorofluoromethane has been estimated to have a half-life of 1.0 hour in a model river, 1 meter deep flowing at 1 m/sec with a wind speed of 3 m/sec, based on the Henry's Law Constant and a recommended equation (HSDB, 2004; Howard, 1993). It has an estimated volatilization half-life from a model lake (1 meter deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec) of 97 hours. This was determined using a recommended equation and an estimated Henry's Law Constant of 1.08 x 10(-2) atm-m(3)/mole, derived from dichlorofluoromethane's vapor pressure of 1.36 x 10(3) mmHg and water solubility of 1.88 x 10(4) mg/L (HSDB, 2004). Rate constants for the neutral and alkaline hydrolysis reactions for dichlorofluoromethane are 2.1 x 10(-10) and 5.4 x 10(-9) L/mole-min, respectively. These rates correspond to a half-life of approximately 230 years (Howard, 1993; HSDB, 2004).
GROUND WATER
TERRESTRIAL As dichlorofluoromethane is an inert gas with a high vapor pressure at room temperature and because it has low soil adsorptive capabilities (estimated Koc of 35), most of the chemical released on land will be lost by volatilization. Dichlorofluoromethane lacks a suitable chromophoric group for absorption of light >290 nm, and it has a low rate of hydrolysis. Therefore, it is unlikely that photooxidation and hydrolysis will be significant in soil. Biodegradation of dichlorofluoromethane in soil is not likely important, based on the biodegradation of similarly structured compounds (Howard, 1993). The estimated Henry's Law Constant indicates rapid volatilization from moist soil surfaces, while the vapor pressure indicates rapid volatilization from dry soil surfaces (HSDB, 2004). The estimated Koc for dichlorofluoromethane of 35 indicates very high mobility in soil and thus a high potential for leaching into groundwater (Howard, 1993; HSDB, 2004).
ABIOTIC DEGRADATION
- Dichlorofluoromethane remains in its gaseous form in the atmosphere. Atmospheric removal occurs by reaction with photochemically-produced hydroxyl radicals and wet deposition. It also diffuses into the troposphere where it contributes to damage of the ozone. Volatilization is the major removal process of dichlorofluoromethane from soil and water. This process contributes to the re-release of the material to air. It has low soil adsorptive capabilities and adsorption to aquatic sediment or suspended solids in the water column is not important (estimated organic carbon partition coefficient, Koc, of 35). The Koc suggests very high mobility in soil and high potential for leaching into groundwater. Hydrolysis, photolysis and biodegradation are not significant (HSDB, 2004; Bingham et al, 2001; Howard, 1993).
BIODEGRADATION
- A soil study using methanotrophic bacteria under aerobic conditions and with the addition of methane to soil samples demonstrated complete biodegradation of dichlorofluoromethane in agricultural soil samples within 19 days (initial soil concentration of 95 ppm) and within 5 days in forest soil samples (initially present at 26 ppm) (HSDB, 2004).
- Anaerobic biodegradation was evaluated where dichlorofluoromethane was added to anoxic sediment samples collected from a freshwater wetland and from a salt water wetland. Approximately 93% biodegradation was observed within 27 days at 20 degrees C in the fresh water sediments, and 50% of the dichlorofluoromethane added to the salt water sediments was degraded in 43 days (no temperature given). Approximately 26% degradation was observed in sterilized controls (HSDB, 2004).
- Anaerobic conditions were also examined in a study where approximately 90% of dichlorofluoromethane was degraded in 24 hours (degradation rate of 0.3 mcmol/hour) by a mixed methanotrophic culture (ENV2041) suspended in a 3-(N-morpholino)-propanesulfonic acid solution at 20 degrees C with a pH of 7.4. Degradation rates of 0.2 and 0.1 were observed using M. trichosporium (OB3b) and M. vaccae (JOB5), respectively (HSDB, 2004).
BIOACCUMULATION
BCFs of 8.9 and 3 have been estimated for dichlorofluoromethane based on a log octanol/water partition coefficient (Kow) of 1.55 and regression-derived equations. These BCF values indicate that the potential for bioconcentration of dichlorofluoromethane in aquatic organisms is low to absent (Howard, 1993; HSDB, 2004).
ENVIRONMENTAL TOXICITY
- No information found at the time of this review.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Dichlorofluoromethane is a colorless, heavy gas. It has a nearly odorless to slight, ether-like odor. It occurs as a liquid below 48 degrees F and is shipped as a liquefied compressed gas or as a liquid under it's own vapor pressure (AAR, 2000; CHRIS , 2002; ILO , 1998; ITI, 1995; Lewis, 1997; Lewis, 2000).
VAPOR PRESSURE
- 1216 mmHg (at 20 degrees C) (Howard, 1993)
- 1.6 atm (at 70 degrees F) (NIOSH , 2002)
- 2 atm (at 28.4 degrees C) (Lewis, 2000)
- 1360 mmHg (at 25 degrees C) (HSDB , 2002)
SPECIFIC GRAVITY
- STANDARD TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
1.48 (at 20 degrees C) (CHRIS , 2002) 1.405 (liquid at 9 degrees C) (ACGIH, 1991; Bingham et al, 2001)
DENSITY
- STANDARD TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
1.405 g/ml (at 9 degrees C) (Relative Density; water =1) (ILO , 1998) 1.405 (liquid density at 9 degrees C) (Bingham et al, 2001)
- TEMPERATURE AND/OR PRESSURE NOT LISTED
BOILING POINT
- 8.9 degrees C; 48 degrees F; 282 K (ACGIH, 1991; CHRIS , 2002; ITI, 1995; Lewis, 1997; Lewis, 2000)
- 8.9 degrees C (at 101.3 kPa; 760 mmHg) (Bingham et al, 2001; Howard, 1993; HSDB , 2002)
- 9 degrees C (Ashford, 1994; ILO , 1998)
AUTOIGNITION TEMPERATURE
- 522 degrees C (ILO , 1998; HSDB , 2002)
- 552 degrees C (ITI, 1995)
- 1022 degrees F (CHRIS , 2002)
SOLUBILITY
Insoluble (ACGIH, 1991; ILO , 1998; ITI, 1995; Lewis, 1997) 9.5 g/L (at 25 degrees C) (Bingham et al, 2001; Howard, 1993; HSDB , 2002) 0.7% (at 86 degrees F) (NIOSH , 2002) 1.88x10(4) mg/L (at 25 degrees C) (HSDB , 2002)
Dichlorofluoromethane is soluble in alcohol, carbon tetrachloride and ether (ACGIH, 1991; HSDB , 2002; ITI, 1995; Lewis, 1997) 69 parts/100 parts acetic acid (HSDB , 2002) 108 parts/100 parts dioxane (HSDB , 2002) >10% in ethyl alcohol (HSDB , 2002) >10% in ethyl ether (HSDB , 2002) >10% in chloroform (HSDB , 2002)
OCTANOL/WATER PARTITION COEFFICIENT
- Log Kow = 1.55 (Howard, 1993; HSDB , 2002)
HENRY'S CONSTANT
- 0.025 atm-m(3)/mol (estimated by the bond method) (Howard, 1993)
SPECTRAL CONSTANTS
OTHER/PHYSICAL
- NUCLEAR MAGNETIC RESONANCE
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