ISOPROPYL ALCOHOL
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
ALCOJEL ALCOOL ISOPROPILICO (Italian) ALCOOL ISOPROPYLIQUE (French) ALCOSOLVE AVANTIN AVANTINE COMBI-SCHUTZ DIMETHYLCARBINOL HARTOSOL (Component of) HIBISTAT 2-HYDROXYPROPANE IPA IMSOL A ISOHOL ISOPROPANOL ISOPROPYL ALCOHOL ISO-PROPYLALKOHOL (German) LUTOSOL 1-METHYLETHANOL 1-METHYLETHYL ALCOHOL PETROHOL PRO PROPAN-2-OL n-PROPAN-2-OL 2-PROPANOL 2-PROPYL ALCOHOL i-PROPYL ALCOHOL i-PROPYLALKOHOL (German) i-PROPANOL (German) SEC-PROPYL ALCOHOL SECONDARY PROPYL ALCOHOL SPECTRAR STERISOL HAND DISINFECTANT VISCO AVINTIN CHROMAR DIMETHYL CARBINOL PARACETAT PROPOL RUBBING ALCOHOL TAKINEOCOL
IDENTIFIERS
1219-Isopropyl alcohol 1219-Isopropanol
SYNONYM REFERENCE
- (HSDB, 2003; RTECS, 2003)
USES/FORMS/SOURCES
Isopropanol is a raw material used for the synthesis of acetone, glycerin, and other chemicals; it is also used as a solvent for oils, gums, creosote, and resins, and as a deicing agent for liquid fuels. A 70% solution of isopropanol in water is widely used as rubbing alcohol. It is also found in skin lotions, hair care and shaving products, some home aerosols, and pharmaceuticals (ACGIH, 2001; Ashford, 2001; Budavari, 1996; Hathaway et al, 1996; Lewis, 2001) . Isopropanol is also used in perfumes, soaps, and window cleaners (AAR, 2000). It is used in foods as a synthetic flavoring adjuvant and in nonalcoholic beverages, candy, and baked goods (HSDB, 2003). Isopropanol is used for medicinal purposes as an antiseptic, disinfectant, in various liniments, tinctures, and tonics, and as a bathing solution for surgical sutures and dressings (HSDB, 2003). Isopropanol may be found in the following products: Frost remover (25% to 100%); liquid detergent (0% to 12%); disinfectant cleaners (6% to 15%); glass window cleaner (0% to 25%); jewelry cleaner (10% to 15%); rubbing alcohol (70%); stain spot remover (10% to 30%) (Zaman et al, 2002a). FOLK MEDICINE: Isopropyl alcohol toxicity developed in a 4-year-old girl who was bathed in a preparation of chamomile and isopropyl alcohol during a Mexican folk healing ritual (curanderismo, to treat evil spirits) (DeBellonia et al, 2008).
Isopropanol is a colorless, flammable liquid with a pleasant odor resembling rubbing alcohol and a slightly bitter taste (ACGIH, 2001; Ashford, 2001; Lewis, 2001; Lewis, 2000)
NOTE: Not all rubbing alcohol contains isopropanol; some rubbing alcohol contains ethanol. Isopropanol is produced from the indirect hydration of propylene and from the treatment of propylene with sulfuric acid (strong acid method). It may also be recovered from aqueous mixtures by salting out with sodium chloride, sodium sulfate, sodium hydroxide, etc (Ashford, 2001; Budavari, 1996; Lewis, 2001). Isopropyl alcohol may form in the postmortem state (Davis et al, 1984). This is presumably the result of bacterial or other putrification processes.
SYNONYM EXPLANATION
- Isopropanol is the legal label name for isopropyl alcohol (Lewis, 2001).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- USES: Primarily used as a topical antiseptic. Typical household preparations contain 70% isopropanol. Also used as a solvent in many household, cosmetic, and topical pharmaceutical products. Isopropanol baths are occasionally used in some cultural practices to relieve fevers.
- TOXICOLOGY: CNS depressant and gastrointestinal (GI) irritant; acetone (metabolite) likely contributes to CNS depression.
- EPIDEMIOLOGY: Isopropyl alcohol exposure is the most common toxic alcohol exposure reported to poison centers in the United States. Cases occur in the thousands per year, but toxicity is rarely severe.
MILD TO MODERATE TOXICITY: May include CNS depression, dysarthria, ataxia, nystagmus, similar to ethanol intoxication, nausea/vomiting, flushing, headache, tachycardia, mild hyperglycemia, ketonuria, and ketonemia WITHOUT metabolic acidosis. Although isopropyl alcohol is metabolized to acetone and does not usually cause metabolic acidosis, metabolic acidosis can occur in patients who drink isopropyl alcohol, experience decreased caloric intake, and develop alcoholic ketoacidosis. SEVERE TOXICITY: May include hemorrhagic gastritis, hypotension, respiratory depression, and coma. Death is rare and likely secondary to respiratory depression and aspiration. EYE EXPOSURE: Splash or vapor exposure can cause irritation, burns, corneal abrasion and ulceration. DERMAL EXPOSURE: Repeated dermal application can cause systemic toxicity (primarily CNS depression), especially in infants and young children, because of more extensive dermal absorption and greater surface area-to-volume ratios. PARENTERAL EXPOSURE: CNS and respiratory depression are possible; hemolysis has developed in 1 patient.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
May cause toxic effects if inhaled or absorbed through skin. Inhalation or contact with material may irritate or burn skin and eyes. Fire will produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control or dilution water may cause pollution.
ACUTE CLINICAL EFFECTS
TOXICOLOGY: CNS depressant and gastrointestinal (GI) irritant; acetone (metabolite) likely contributes to CNS depression. EPIDEMIOLOGY: Isopropyl alcohol exposure is the most common toxic alcohol exposure reported to poison centers in the United States. Cases occur in the thousands per year, but toxicity is rarely severe. MILD TO MODERATE TOXICITY: May include CNS depression, dysarthria, ataxia, nystagmus, similar to ethanol intoxication, nausea/vomiting, flushing, headache, tachycardia, mild hyperglycemia, ketonuria, and ketonemia WITHOUT metabolic acidosis. Although isopropyl alcohol is metabolized to acetone and does not usually cause metabolic acidosis, metabolic acidosis can occur in patients who drink isopropyl alcohol, experience decreased caloric intake, and develop alcoholic ketoacidosis. SEVERE TOXICITY: May include hemorrhagic gastritis, hypotension, respiratory depression, and coma. Death is rare and likely secondary to respiratory depression and aspiration. EYE EXPOSURE: Splash or vapor exposure can cause irritation, burns, corneal abrasion and ulceration. DERMAL EXPOSURE: Repeated dermal application can cause systemic toxicity (primarily CNS depression), especially in infants and young children, because of more extensive dermal absorption and greater surface area-to-volume ratios. PARENTERAL EXPOSURE: CNS and respiratory depression are possible; hemolysis has developed in 1 patient.
- Isopropanol can be absorbed in toxic amounts by ingestion, inhalation, and through intact skin (Dhillon & Von Burg, 1995). It is an irritant and mild CNS depressant (ACGIH, 1992) (Hathaway et al, 1991; Kapp et al, 1996). The no-effect level with inhalation exposure has been reported to be 200 parts per million (ppm)/8 hours (EPA, 1979). As little as 0.5 mg/kg may cause symptoms, but adults have survived oral doses as high as 1 L. Alcoholics have a higher tolerance (Dhillon & Von Burg, 1995).
- Symptoms of overexposure include headache, drowsiness, loss of coordination (NIOSH/OSHA), hypotension, hypothermia, kidney and liver dysfunction, coma, and death in respiratory arrest (EPA, 1979). Inhalation exposure to airborne concentrations up to 400 ppm has caused mild eye, nose, and throat irritation, whereas inhalation of 800 ppm produced more intense signs and symptoms (ACGIH, 1992; (Hathaway et al, 1991; Dhillon & Von Burg, 1995). No cases of acute occupational poisoning have been reported (Hathaway et al, 1991).
- Isopropanol is absorbed through intact skin and has caused unconsciousness in a child exposed to a large amount (12 ounces covered with a towel) (HSDB). If splashed in the eye, it can cause corneal burns (Sax, 1984). Isopropanol can be fatal if as little as 100 mL is ingested (Sax, 1984). Pulmonary aspiration with resultant chemical pneumonitis may also occur (EPA, 1979). An isopropanol enema led to coma and death in 1 case (Haviv et al, 1998).
- One case of acute isopropanol exposure without clinical signs and symptoms has been reported in a patient who had a serum concentration of 72 mmol/L. The estimated half-life for elimination was 5 to 7 hours, and no acetone was detected over a 5-day period (Chan et al, 1993). The elimination half-life was relatively rapid in a person who had ingested isopropanol: t(1/2) of 1 to 3 hours vs 17 to 27 hours for its metabolite, acetone (Jones & Summers, 2000).
- In a newborn infant with acute isopropanol poisoning, the estimated elimination half-life was 9.6 hours. Twelve-and-a-half hours after exposure, the infant developed cyanosis, bradycardia, hypotension, and died (Vicas & Beck, 1993).
- In rats exposed by inhalation, acute neurotoxicity was noted at 1 and 6 hours at 5000 ppm, but only minimal effects were seen at 1500 ppm and the animals recovered within 5 hours. No toxicity was noted at 500 ppm (Gill et al, 1995).
- Isopropanol was absorbed by the dermal route in rats; the mean elimination half-life followed first-order kinetics and was 0.8 to 0.9 hours for isopropanol and 2.1 to 2.2 hours for acetone (Boatman et al, 1998).
CHRONIC CLINICAL EFFECTS
- Repeated skin contact with isopropanol can cause defatting dermatitis with drying and cracking; rare cases of allergic contact dermatitis have been reported (NIOSH/OSHA). Isopropanol is a dermal sensitizer (Fregert et al, 1971; (Jensen, 1981). Cross-reactivity to butanol and n-propanol have been reported (Ludwig & Hausen, 1977). Allergic keratoconjunctivitis has also been reported after eye contact with isopropanol (Sheretz et al, 1991). An occupational study reported an increase in upper respiratory tract diseases and high blood pressure (Guseinov, 1985), but these have not been confirmed.
- Daily ingestion of doses as high as 6.4 mg/kg for 6 weeks produced no apparent ill effects in human volunteers (Dhillon & Von Burg, 1995).
- Repeated isopropanol exposure in experimental animals produced no irreversible effects (Kapp et al, 1996).
- Ataxia and microscopic hyaline droplets in the kidneys were seen in rats exposed to isopropanol at airborne concentrations up to 5000 ppm for 6 hours per day, 5 days per week, for 13 weeks (Burleigh-Flayer et al, 1994b; Burleigh-Flayer et al, 1997).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
- The onset of CNS depression usually occurs within 30 minutes of ingestion (Lacouture et al, 1983). Do not induce vomiting.
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.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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 substance, immediately flush skin or eyes with running water for at least 20 minutes. Wash skin with soap and water. Keep victim warm and quiet. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. 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.
FIRST AID GENERAL 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.
DERMAL EXPOSURE 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.
ORAL EXPOSURE
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
- The probable oral lethal dose is 240 to 250 mL, although as little as 100 mL can be fatal, and ingestion of only 20 mL has caused poisoning (ACGIH, 2001; Lewis, 2000).
MAXIMUM TOLERATED EXPOSURE
Tests on human subjects found that airborne concentrations of 400 parts per million (ppm) caused mild irritation of the eyes, nose, and throat; at 800 ppm, the irritation was not severe, but the majority of subjects found the concentration uncomfortable (ACGIH, 2001; Hathaway et al, 1996). An adult survived after ingesting 1000 mL of 70% isopropyl alcohol solution (rubbing compound). Hemodialysis and supportive medical treatment were provided (Freireich et al, 1967). Adults have survived with serum isopropyl alcohol levels of 200 mg/dL with supportive care (Natowicz et al, 1985). Hemodialyzed patients have survived with serum levels of up to 560 mg/dL (Alexander et al, 1982). Chronic alcoholics may tolerate very high levels of isopropyl alcohol without development of significant CNS depression (Mendelson et al, 1957).
Pediatric patients have survived (with supportive care) the following serum levels: 128 mg/dL (Senz & Goldfarb, 1958), 130 mg/dL (Wise, 1969), 200 mg/dL (McFadden & Haddow, 1969), 520 mg/dL (Visudhiphan & Kaufman, 1971).
A 21-day-old infant survived (with supportive medical treatment) an estimated dermal exposure to 177 mL of 70% isopropyl alcohol (rubbing alcohol) applied to the umbilicus over a period of 3 weeks. Urinary isopropyl alcohol and acetone levels were 39 mg/dL and 76 mg/dL of acetone, respectively. Serum isopropyl alcohol and acetone concentrations were 8 mg/dL and 203 mg/dL, respectively, 17 hours after admission (Vivier et al, 1994).
- Carcinogenicity Ratings for CAS67-63-0 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Isopropanol ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: 2-Propanol 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): 3 ; Listed as: Isopropanol 3 : The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.
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): 1 ; Listed as: Isopropanol manufacture (strong-acid process) 1 : The agent (mixture) is carcinogenic to humans. The exposure circumstance entails exposures that are carcinogenic to humans. This category is used when there is sufficient evidence of carcinogenicity in humans. Exceptionally, an agent (mixture) may be placed in this category when evidence of carcinogenicity in humans is less than sufficient but there is sufficient evidence of carcinogenicity in experimental animals and strong evidence in exposed humans that the agent (mixture) acts through a relevant mechanism of carcinogenicity.
NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Isopropyl alcohol 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 CAS67-63-0 (U.S. Environmental Protection Agency, 2011):
CALCULATIONS
1 ppm = 2.5 mg/m(3) (Verschueren, 1997) 1 mg/m(3) = 0.408 ppm (Verschueren, 1997)
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS67-63-0 (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. Adopted Value Adopted Value
- AIHA WEEL Values for CAS67-63-0 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS67-63-0 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS67-63-0 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS67-63-0 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS67-63-0 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS67-63-0 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS67-63-0 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS67-63-0 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS67-63-0 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Isopropyl alcohol (Only persons who manufacture by the strong acid process are subject, no supplier notifiction.) Effective Date for Reporting Under 40 CFR 372.30: 1/1/87 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS67-63-0 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS67-63-0 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1219 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1219 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS67-63-0 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
Isopropanol is a very dangerous fire hazard when exposed to heat or flame. Sources of ignition such as smoking and open flames are prohibited where isopropanol is used, handled, or stored. It is also toxic by ingestion and inhalation. Wear appropriate personal protective clothing to prevent prolonged or repeated exposure; remove clothing immediately if wet or contaminated to avoid fire hazard. Use only non-sparking tools and equipment, especially when opening and closing containers (Lewis, 2001; Lewis, 2000; Pohanish, 2002).
HANDLING
- Use only non-sparking tools and equipment, especially when opening and closing containers of isopropanol (Pohanish, 2002).
STORAGE
Store in tightly closed containers. Metal containers involving the transfer of 5 gallons or more of isopropanol should be grounded and bonded. Drums must be equipped with self-closing valves, pressure vacuum bungs, and flame arresters (Sittig, 1991).
- ROOM/CABINET RECOMMENDATIONS
Isopropanol forms an explosive mixture with air. It is incompatible with alkaline earth and alkali metals, crotonaldehyde, phosgene, strong acids, amines, ammonia, caustics, and strong oxidizers. It reacts with metallic aluminum at high temperatures (Lewis, 1996; NFPA, 1994; Pohanish & Greene, 1997; Pohanish, 2002).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- Isopropanol is toxic by inhalation and mildly toxic through skin contact. Avoid breathing vapors; keep upwind of an isopropanol fire or spill. Wear appropriate chemical protective clothing, including gloves, boots, and goggles to prevent repeated or prolonged skin contact. Do not handle broken containers unless wearing protective clothing. Promptly wash away any isopropanol which may have contacted the body with copious amounts of water or soap and water. Remove clothing immediately to avoid fire hazard (AAR, 1996; (Lewis, 1993; Lewis, 1996; Pohanish, 2002).
EYE/FACE PROTECTION
- Wear eye protection to prevent any reasonable probability of eye contact (Pohanish, 2002).
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
- Avoid breathing vapors; keep upwind (AAR, 1996).
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 67-63-0.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004) HIGHLY FLAMMABLE: Will be easily ignited by heat, sparks or flames. Vapors may form explosive mixtures with air. Vapors may travel to source of ignition and flash back. Most vapors are heavier than air. They will spread along ground and collect in low or confined areas (sewers, basements, tanks). Vapor explosion hazard indoors, outdoors or in sewers. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Runoff to sewer may create fire or explosion hazard. Containers may explode when heated. Many liquids are lighter than water.
Isopropanol is a very dangerous fire hazard when exposed to heat, flame, or oxidizers; it may be easily ignited over a wide range of ambient temperature conditions. It is moderately explosive when exposed to heat or flame (Lewis, 1993; Lewis, 1996). If isopropanol is involved in a fire, do not try to extinguish the fire unless the flow of isopropanol can be stopped. Use water in flooding quantities as fog; solid streams of water may be ineffective. Cool all affected containers with flooding quantities of water; apply water from as far a distance as possible. Use "alcohol" foam, dry chemical, or carbon dioxide to extinguish the fire (AAR, 1996; ITI, 1988; (Sittig, 1991).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS67-63-0 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Dry chemical, CO2, water spray or alcohol-resistant foam. Do not use dry chemical extinguishers to control fires involving nitromethane or nitroethane.
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Water spray, fog or alcohol-resistant foam. Do not use straight streams. Move containers from fire area if you can do it without risk.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS67-63-0 (NFPA, 2002):
Listed as: Isopropyl Alcohol, 88% Extinguishing Method(s): 5, 1 5: Flammable liquid fires can be extinguished using carbon dioxide, dry chemical, foam, and vaporizing liquid extinguishers, as long as the fires are small to moderate in size and the flammable liquid reservoir is shallow. Use of foam to form a blanket over a flammable liquid is not effective when the liquid is water-soluble. Certain alcohol resistant foams are effective extinguishing agents for polar, non-polar, and water-soluble liquid fires. These foams are preferred for fighting flammable liquid fires except those that involve water reactive flammable liquids. 1: "Water may be ineffective" applies to a situation where materials with a flash point below 100 degrees F (37.8 degrees C) are burning. Water will only be effective if used by experienced fire fighters under favorable conditions. Even though water may not put the fire out, it can be used to protect equipment and structures.
EXPLOSION HAZARD
- Isopropanol is moderately explosive when exposed to heat or flame; it forms an explosive mixture with air (Lewis, 1996; Pohanish & Greene, 1997).
- Refer to the REACTIVITY HAZARD Section for complete information.
DUST/VAPOR HAZARD
- The vapors are mildly irritating to the eyes, nose, and throat. At warmer temperatures, isopropanol vapors may travel some distance to a source of ignition and flash back. Accumulations of vapor in confined spaces such as buildings or sewers may explode if ignited; use water spray to disperse vapors (AAR, 1996; (Sittig, 1991).
- When heated to decomposition, isopropanol emits acrid smoke and fumes (Lewis, 1996).
REACTIVITY HAZARD
- Isopropanol forms an explosive mixture with air (Pohanish & Greene, 1997).
It reacts with oxygen to form dangerously unstable peroxides which can concentrate and explode during distillation or evaporation. The presence of 2-butanone increases the reaction rate for peroxide formation. Hydrogen peroxide sharply reduces the autoignition temperature (Lewis, 1996; NFPA, 1994; Urben, 1995).
- Isopropanol is incompatible with alkaline earth and alkali metals, crotonaldehyde, phosgene, strong acids, amines, ammonia, caustics, and strong oxidizers (Pohanish & Greene, 1997; Urben, 1995).
It forms explosive mixtures with trinitromethane and hydrogen peroxide (Lewis, 1996). In general, explosive behavior is noted with hydrogen peroxide when the ratio of hydrogen peroxide to water is greater than 1, and, if the overall fuel-peroxide composition is stoicheiometric the explosive power and sensitivity may be equivalent to glyceryl nitrate (Urben, 1995).
It reacts with barium perchlorate to form the highly explosive propyl perchlorate (Lewis, 1996). After a delay, isopropanol ignites on contact with dioxgenyl tetrafluoroborate, chromium trioxide, and potassium tert-butoxide (Lewis, 1996; Urben, 1995). It also has a delayed, vigorous reaction with sodium dichromate + sulfuric acid and aluminum (Lewis, 1996). It reacts violently with hydrogen + palladium, nitroform, oleum, COCl2, aluminum triisopropoxide, and oxidants. It can react vigorously with oxidizing materials (Lewis, 1996; NFPA, 1994). The reaction between isopropanol and phosgene forms isopropyl chloroformate and hydrogen chloride. In the presence of iron salts thermal decomposition can occur which may become explosive (NFPA, 1994)
- Isopropanol reacts with metallic aluminum at high temperatures (Pohanish & Greene, 1997).
- Isopropanol attacks some plastics, rubber, and coatings (Pohanish & Greene, 1997).
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 129 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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 129 (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 50 meters (150 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate closed spaces before entering.
- If isopropanol is leaking and not on fire, consider evacuation from downwind areas based on the amount of spilled isopropanol, location of the spill, and the weather conditions (AAR, 1996).
- AIHA ERPG Values for CAS67-63-0 (AIHA, 2006):
- DOE TEEL Values for CAS67-63-0 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Isopropyl alcohol TEEL-0 (units = ppm): 400 TEEL-1 (units = ppm): 400 TEEL-2 (units = ppm): 400 TEEL-3 (units = ppm): 2,000 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 CAS67-63-0 (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 CAS67-63-0 (National Institute for Occupational Safety and Health, 2007):
IDLH: 2000 ppm Note(s): [10%LEL]
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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 or walk through spilled material. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. A vapor suppressing foam may be used to reduce vapors. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. Use clean non-sparking tools to collect absorbed material.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004) If isopropanol in not on fire and not involved in a fire, keep sparks, flames, and other sources of ignition away from the spill and ventilate the area. Keep people not wearing appropriate protective clothing and equipment away from the spill area. Keep isopropanol out of water sources and sewers; build dikes as necessary to contain the flow. Attempt to stop the leak if this can be done without undue personnel hazard. Absorb isopropanol with vermiculite, dry sand, earth, or a similar material and deposit in sealable containers. Use water spray to disperse vapors and dilute standing pools of isopropanol (AAR, 1996; (Sittig, 1991). "At the time of this review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices." (HSDB , 1999)
Incineration is a suggested disposal method (Sittig, 1991). There are published studies which have demonstrated the use of high-temperature air stripping to remove isopropanol from contaminated groundwater (Freeman, 1989). Waste management activities associated with material disposition are unique to individual situations. Proper waste characterization and decisions regarding waste management should be coordinated with the appropriate local, state, or federal authorities to ensure compliance with all applicable rules and regulations.
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Isopropanol will primarily enter the environment as emissions from its manufacture and use as a solvent. It also occurs from emissions from petroleum storage, auto exhaust, plastics combustion, printing, sewage treatment, wood pulping, steel manufacturing, and from the use of consumer products. It may be found in leachate from landfills, and in wastewater from shale tar distillation. Isopropanol naturally occurs as a plant volatile and is released during the microbial degradation of animal wastes and emitted from volcanoes (Howard, 1990).
ENVIRONMENTAL FATE AND KINETICS
When released into the atmosphere, isopropanol will photodegrade with an estimated half-life ranging from one to several days. Based on its solubility in water, rainout may be significant (Howard, 1990).
TERRESTRIAL When released to soil, isopropanol will evaporate quickly and leach into the ground due to its high vapor pressure and low adsorption to soil. If soil degradation is not rapid, it is expected to leach into groundwater (Howard, 1990).
ABIOTIC DEGRADATION
- The estimated half-life of isopropanol in the atmosphere ranges from 33 hours to 3.5 days based on a hydroxyl ion concentration of 0.8x10(6) molecules/cm(3). Isopropanol is considered to have low reactivity in photochemical smog situations; a 20% decrease in isopropanol was observed after 5 hours in a smog chamber at 30 degrees C containing 2 ppm isopropanol and 1 ppm nitrous oxide at 55% relative humidity. Since alcohols are known to be resistant to hydrolysis, reaction with hydroxyl radicals in aquatic media will not likely be significant (Howard, 1990).
The atmospheric photolysis half-life is not expected to be significant (Howard et al, 1991). The photooxidation half-life of isopropanol in water ranges from 4728 hours (197 days) to 1.9x10(5) hours (22 years) based on measured rates for reaction with hydroxyl radicals in water (Howard et al, 1991). The photooxidation half-life of isopropanol in air ranges from 6.2 hours (0.26 days) to 72 hours (3 days) based on measured rates for reaction with hydroxyl radicals in air (Howard et al, 1991).
BIODEGRADATION
- Degradation with sewage at 20 degrees C for 5 days resulted in 58% theoretical BOD (average of 4 results). Filtered sewage seed resulted in 49% theoretical BOD and acclimated sewage seed resulted in 72% of theoretical BOD after 5 days. Concentrations of 3, 7, and 10 mg/L with filtered sewage seed in fresh water resulted in 28% theoretical BOD in 5 days and 78% in 20 days; in salt water, 13% theoretical BOD in 5 days and 72% in 20 days was observed (Howard, 1990).
The scientific judgement of the half-life of isopropanol ranges from 24 hours (1 day) to 168 hours (7 days) based on the estimated unacclimated aerobic aqueous biodegradation half-life (Howard et al, 1991). The scientific judgement of the half-life of isopropanol ranges from 96 hours (4 days) to 672 hours (28 days) based on the estimated aqueous aerobic biodegradation half-life and unacclimated anaerobic aqueous screening test data (Howard et al, 1991).
- An anaerobic bacterium that degraded alcohols and polyols was isolated in pure culture and characterized. The isolate was identified as a member of the genus Desulfovibrio and found to reduce sulfate, sulfite, thiosulfate, and elemental sulfur with accompanying growth. Isopropanol was oxidized to its respective ketone (Tenaka, 1992).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- Ecotoxicity Values (HSDB , 1999):
LD50 - Carassius auratus/Goldfish: >5000 mg/L for 24H -- modified ASTM D 1345 bioassay LC50 - Poecilia reticulata/Guppies: 7060 ppm for 7D -- conditions of bioassay not specified LC50 - Crangon crangon/Brown Shrimp: 1400 mg/L for 48H -- Range 900-1950 mg/L, conditions of bioassay not specified LC50 - Crangon crangon/Brown Shrimp: 1150 mg/L for 96H -- Range 750-1650 mg/L, conditions of bioassay not specified LC50 - Pimephales promelas/Fathead Minnows: 11,830 mg/L for 1H -- static bioassay in Lake Superior water, 18-22 degrees C LC50 - Pimephales promelas/Fathead Minnows: 11,160 mg/L for 24H -- static bioassay in Lake Superior water, 18-22 degrees C LC50 - Pimephales promelas/Fathead Minnows: 11,130 mg/L for 48H, 72H, 96H -- static bioassay in Lake Superior water, 18-22 degrees C LC50 - Pimephales promelas/Fathead Minnows: 9.64 g/L for 96H -- 31 days old, 24.4 degrees C, flow-through bioassay LC50 - Pimephales promelas/Fathead Minnows: 10.4 g/L for 96H -- 29 days old, 24.6 degrees C, flow-through bioassay LC50 - Pimephales promelas/Fathead Minnows: 6.55 g/L for 96H -- 31 days old, 24.6 degrees C, flow-through bioassay LC50 - Pimephales promelas/Fathead Minnows: 9.54 g/L for 96H -- 31 days old, 24.4 degrees C, flow-through bioassay LC50 - Pimephales promelas/Fathead Minnows: 6.12 g/L for 96H -- 31 days old, 24.6 degrees C, flow-through bioassay LC50 - Pimephales promelas/Fathead Minnows: 9.49 g/L for 96H -- 29 days old, 24.4 degrees C, flow-through bioassay LD100 - Semolitus atromaculatus/Creek Chub: 1100 mg/L for 24H -- in Detroit River water, conditions of bioassay not specified
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Isopropanol is a colorless, flammable liquid with a slight odor resembling rubbing alcohol and a slightly bitter taste (ACGIH, 2001; Ashford, 2001; Budavari, 1996; Lewis, 2001; Lewis, 2000).
PH
VAPOR PRESSURE
- 32 mmHg (at 20 degrees C) (Verschueren, 1983)
- 33 mmHg (at 20 degrees C) (ACGIH, 1991; Lewis, 2001)
- 43 mmHg (at 25 degrees C) (Howard, 1990)
- 57 mmHg (at 30 degrees C) (Verschueren, 1983)
SPECIFIC GRAVITY
- NORMAL TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
0.785 (at 20/4 degrees C) (Verschueren, 1983) 0.78505 (at 20/4 degrees C) (Budavari, 1996) 0.728 (at 83/4 degrees C) (Budavari, 1996) 0.7863 (at 20/20 degrees C) (Lewis, 2001) 0.79 (at 20/20 degrees C) (ITI, 1995)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
0.78 kg/L (at 20 degrees C) (Ashford, 2001) 0.7861 kg/L (at 20 degrees C) (ACGIH, 2001)
FREEZING/MELTING POINT
-89 degrees C (Ashford, 1994) -89.5 degrees C (ACGIH, 1991; Budavari, 1996)
-86 to -89 degrees C (Verschueren, 1983) -88.5 degrees C (Budavari, 1996; Howard, 1990) -88.5 to -89.5 degrees C (Lewis, 2000)
BOILING POINT
- 82.4 degrees C (at 760 mmHg) (ACGIH, 1991; Lewis, 2001; Verschueren, 1983)
- 82.5 degrees C (at 760 mmHg) (Budavari, 1996; Howard, 1990; Lewis, 2000)
- 83 degrees C; 181 degrees F (NFPA, 1994)
- 67.8 degrees C (at 400 mmHg) (Budavari, 1996)
- 53.0 degrees C (at 200 mmHg) (Budavari, 1996)
- 39.5 degrees C (at 100 mmHg) (Budavari, 1996)
- 30.5 degrees C (at 60 mmHg) (Budavari, 1996)
- 23.8 degrees C (at 40 mmHg) (Budavari, 1996)
- 12.7 degrees C (at 20 mmHg) (Budavari, 1996)
- 2.4 degrees C (at 10 mmHg) (Budavari, 1996)
- -7.0 degrees C (at 5 mmHg) (Budavari, 1996)
- -26.1 degrees C (at 1.0 mmHg) (Budavari, 1996)
FLASH POINT
- 11.7 degrees C; 53 degrees F (closed cup) (ACGIH, 1991; Budavari, 1996; Lewis, 1996)
- 11.7 degrees C; 53 degrees F (Tagliabue Open Cup) (Lewis, 2001)
- 15 degrees C (Tagliabue Closed Cup) (Ashford, 1994)
- 18.3 degrees C (open cup) (ACGIH, 1991)
AUTOIGNITION TEMPERATURE
- 399 degrees C; 750 degrees F (ACGIH, 1991; NFPA, 1994)
- 453 degrees C; 850 degrees F (Lewis, 2001)
- 455.6 degrees C; 852 degrees F (Budavari, 1996; Lewis, 2000)
EXPLOSIVE LIMITS
SOLUBILITY
Isopropanol is miscible with water (ACGIH, 2001; Ashford, 2001; Budavari, 1996; Lewis, 2001; Lewis, 2000).
Isopropanol is miscible with most organic solvents including alcohol, ether, chloroform, ethyl alcohol and ethyl ether (ACGIH, 2001; Ashford, 2001; Budavari, 1996; Lewis, 2001; Lewis, 2000).
OCTANOL/WATER PARTITION COEFFICIENT
- log -0.16 to 0.28 (calculated) (Verschueren, 1983)
HENRY'S CONSTANT
- 8.07x10(-6)atm-m(3)/mol (Howard, 1990)
SPECTRAL CONSTANTS
OTHER/PHYSICAL
20.8 dynes/cm (at 25 degrees C) (HSDB, 2003) 0.0214 mN/m (at 20 degrees C) (HSDB, 2003)
53 atm (Lewis, 2001) 47 atm (HSDB , 1999)
18.3 (at 25 degrees C) (HSDB, 2003) 16.24 (at 40 degrees C) (HSDB, 2003)
14,346 Btu/lb (Lewis, 1993) 474.8 kg cal/g mol wt (at 20 degrees C)
1.3756 (at 20 degrees C) (Lewis, 2001) 1.3772 (at 20 degrees C) (ITI, 1995) 1.37723 (at 20 degrees C) (Budavari, 1996) 1.3802 (at 15 degrees C) (Budavari, 1996) 1.3852 (at 8 degrees C) (Budavari, 1996) 1.3769 (at 20 degrees C and sodium light) (HSDB, 2003)
- NUCLEAR MAGNETIC RESONANCE
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