BUTANOL
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
BUTANOL BUTYL ALCOHOL ALCOOL BUTYLIQUE (French) BUTANOL (French) n-BUTANOL 1-BUTANOL BUTAN-1-OL N-BUTAN-1-OL BUTANOLEN (Dutch) BUTANOLO (Italian) n-BUTYL ALCOHOL BUTYL HYDROXIDE BUTYLOWY ALKOHOL (Polish) BUTYRIC ALCOHOL CCS 203 HEMOSTYP 1-HYDROXYBUTANE METHYLOLPROPANE NORMAL PRIMARY BUTYL ALCOHOL PROPYLCARBINOL PROPYLMETHANOL
IDENTIFIERS
SYNONYM REFERENCE
- (Lewis, 1996; HSDB , 2000; RTECS , 2000)
USES/FORMS/SOURCES
Butanol is used as an industrial solvent or cosolvent for fats, resins, gums, waxes, lacquer thinners, coatings, paints, and inks, as an extractant for minerals, antibiotics, hormones, vitamins, hops, and vegetable oils, and as a chemical intermediate in the manufacture of lacquers, rayons, herbicides, detergents, and other butyl compounds (Ashford, 1994) Baselt, 1997; (Budavari, 1996; Clayton & Clayton, 1994; Harbison, 1998; Hathaway et al, 1996; Lewis, 1997; Raffle et al, 1994; Snyder, 1992).
It is a colorless, volatile, highly refractive liquid which burns with a strongly luminous flame. Its odor has been described as like fusel oil but weaker, as rancid, and as vinous (Ashford, 1994; Budavari, 1996; Clayton & Clayton, 1994; Hathaway et al, 1996; Lewis, 1996; Lewis, 1997; Lewis, 1998; Snyder, 1992; Verschueren, 1983).
Butanol is produced by the hydrogenation of n-butyraldehyde or crotonaldehyde, by the addition of propylene and synthesis gas, and by the fractionation of oxygenates. It occurs in natural sources such as peppermint oil, some teas, apple aromas, and the bacteria strains Clostridium butylicum, and Clostridium acetobutylicum (Ashford, 1994; Clayton & Clayton, 1994; Harbison, 1998; Howard, 1990; Lewis, 1997).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- The main routes of occupational exposure are inhalation and skin and eye contact. Exposure to vapors for short periods irritates eyes, nose, throat and mucous membranes and produces respiratory inflammation, headaches and dizziness. Burning, red eyes with corneal inflammation, blurred vision, tearing, light sensitivity and keratitis can result, as well as dry cracked skin and dermatoid eczematoid dermatitis.
- Central nervous system depression can result from exposure to high concentrations. Extended exposure can produce hearing impairment, with auditory nerve damage and vestibular injury. Butanol may be absorbed through the skin.
- Human exposure also occurs through ingestion. Alcohol intoxication and narcosis with drowsiness, ataxia, confusion, delirium, paralysis, muscle weakness, nausea and vomiting and possibly coma can result. Butanol is poisonous intravenously.
- 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
- Butanol is an irritant of the throat, eyes, and skin (ILO, 1983). It causes tearing, blurred vision, and inflammation of the cornea (HSDB). The lowest exposure producing irritant effects has been reported to be approximately 50 ppm, with exposures to greater than 200 ppm resulting in a decreased blood count (ILO, 1983).
CHRONIC CLINICAL EFFECTS
- Subchronic or chronic occupational butanol exposures have been associated with cough, headache, dizziness, drowsiness, damage to the auditory nerve (with some hearing loss), and vestibular injury (HSDB). Butanol has been reported to produce severe vertigo, diagnosed as Meniere's disease (Seitz, 1972). This pattern of symptoms is consistent with its action as a CNS depressant; however, the severity of the vertigo and damage to the auditory nerve may be specific rather than general effects.
- In a Russian study, 0.1 mg/m(3) was the no effect level to prevent neurological effects in humans (Bankov & Hacaturjan, 1973). As this corresponds to only 0.03 ppm, it may be questionable if this value is correct.
- Butanol has caused EEG changes in mice (pp 16-22). A possible cause for concern is accumulation of butanol in a metabolic study in rats (Rumyantsev, 1975). Whether it can accumulate in humans as a result of chronic exposure is not known.
-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 EYE EXPOSURE - Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Contact lenses should not be worn when working with this chemical. DERMAL EXPOSURE - Flush the contaminated skin with water promptly. If this chemical penetrates the clothing, immediately remove the clothing and flush the skin with water promptly. If irritation persists after washing, get medical attention. 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. ORAL EXPOSURE - If this chemical has been swallowed, get medical attention immediately. TARGET ORGANS - Eyes, skin, respiratory system, central nervous system (National Institute for Occupational Safety and Health, 2007).
GENERAL - Move victims of inhalation exposure from the toxic environment and administer 100% humidified supplemental oxygen with assisted ventilation as required. Exposed skin and eyes should be copiously flushed with water. Because of the potential for rapid onset of CNS depression or seizures with possible aspiration of gastric contents, EMESIS SHOULD NOT BE INDUCED. Cautious gastric lavage followed by administration of activated charcoal may be of benefit if the patient is seen soon after the exposure.
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.
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 - Because of the potential for central nervous system depression, DO NOT induce emesis. DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
The minimum lethal human dose to this agent has not been delineated. Acute human exposure to butanol causes irritation to the eyes, mucous membranes, and to the skin. Other symptoms of high exposure may include symptoms which appear to be alcohol intoxication such as dizziness, headaches, and drowsiness (CNS depression). Sometimes, hearing may be affected as well as the ability of the eye to adapt to light (Clayton & Clayton, 1994; Hathaway et al, 1996; Lewis, 1996; Lewis, 1998; Raffle et al, 1994; Snyder, 1992). Butanol vapor may be a more potent CNS depressant than ethanol or isopropanol (Baselt, 1997). Exposure to 25 ppm for 3-5 minutes resulted in mild irritation of the nose and throat. Exposure to concentrations greater than 50 ppm resulted in complaints of eye, nose, and throat irritation, headache and vertigo, and dermatitis on the fingers and hands. Exposure to 200 ppm or more resulted in severe eye irritation including a burning sensation, blurred vision, lachrymation, and photophobia; however, exposures to less than 100 ppm appear to have no systemic effects (Baselt, 1997; (Clayton & Clayton, 1994; Harbison, 1998; Hathaway et al, 1996).
MAXIMUM TOLERATED EXPOSURE
Chronic exposure may result in increased sensitization to butanol's irritating effects, but no chronic effects have been associated with butanol exposure (Clayton & Clayton, 1994; Harbison, 1998) Snyder, 1994).
- Carcinogenicity Ratings for CAS71-36-3 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: n-Butanol EPA (U.S. Environmental Protection Agency, 2011): D ; Listed as: n-Butanol 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: n-Butyl 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 CAS71-36-3 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 1x10(-1) mg/kg-day
Inhalation: Drinking Water:
References: RTECS, 2000 LC50- (INHALATION)RAT: LD50- (INTRAPERITONEAL)MOUSE: LD50- (INTRAVENOUS)MOUSE: LD50- (ORAL)MOUSE: LD50- (SUBCUTANEOUS)MOUSE: LD50- (ORAL)RABBIT: 3484 mg/kg -- Sense Organs and Special Senses (Nose, Eye, Ear, and Taste) - Corneal damage; Cardiac - Pulse rate; Lung, Thorax, or Respiration - Dyspnea
LD50- (SKIN)RABBIT: LD50- (INTRAPERITONEAL)RAT: LD50- (INTRAVENOUS)RAT: LD50- (ORAL)RAT: LDLo- (INTRAVENOUS)CAT: LDLo- (ORAL)DOG: LDLo- (SUBCUTANEOUS)DOG: TCLo- (INHALATION)HUMAN: 25 ppm -- Sense Organs and Special Senses (Nose, Eye, Ear, and Taste) - Other changes; Sense Organs and Special Senses (Nose, Eye, Ear, and Taste) - Conjunctive irritation; Lung, Thorax, or Respiration - Other changes
TCLo- (INHALATION)MOUSE: TCLo- (INHALATION)RAT: Female, 6000 ppm for 7H at 1-19D of pregnancy -- Effects on Embryo or Fetus - Fetotoxicity (except death, e.g., stunted fetus) Female, 8000 ppm for 7H at 1-19D of pregnancy -- Specific Developmental Abnormalities - Musculoskeletal system 6600 mcg/m(3) for 24H/17W- continuous -- Brain and Coverings - Recordings from specific arc-as of CNS; Vascular - Regional or general arteriolar or venous dilation; Liver - Liver function tests impaired
TDLo- (ORAL)RAT: Female, 23,100 mg/kg at 8W prior to mating and 0-20D of pregnancy -- Specific Developmental Abnormalities - Craniofacial (including nose and tongue); Specific Developmental Abnormalities - Musculoskeletal system Female, 35,295 mg/kg at 1-15D of pregnancy -- Effects on Embryo or Fetus - Fetotoxicity (except death, e.g., stunted fetus); Effects on Newborn - Biochemical and metabolic Female, 35,295 mg/kg at 1-15D of pregnancy -- Effects on Fertility - Female fertility index (e.g., # females pregnant per # sperm positive females; # females pregnant per # females mated); Effects on Fertility - Pre-implantation mortality (e.g., reduction in number of implants per female; total number of implants per corpora lutea); Effects on Fertility - Post-implantation mortality (e.g., dead and or resorbed implants per total number of implants) 7 mL/kg for 7D-intermittent -- Liver - Other changes; Biochemical - B vitamin including folate 46,500 mg/kg for 13W- intermittent -- Behavioral - Somnolence (general depressed activity); Behavioral - Ataxia; Blood - Changes in erythrocyte (RBC) count
TDLo- (SUBCUTANEOUS)RAT:
CALCULATIONS
1 mg/L = 330 ppm (Clayton & Clayton, 1994) 1 mg/m(3) = 0.33 ppm (Verschueren, 1983) 1 ppm = 3.03 mg/m(3) (Clayton & Clayton, 1994; Verschueren, 1983)
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS71-36-3 (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 CAS71-36-3 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS71-36-3 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS71-36-3 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS71-36-3 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS71-36-3 (U.S. Environmental Protection Agency, 2010):
Listed as: n-Butyl alcohol Final Reportable Quantity, in pounds (kilograms): Additional Information: The following spent non-halogenated solvents and the still bottoms from the recovery of these solvents. (F003) Listed as: 1-Butanol Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: n-Butyl alcohol Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS71-36-3 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS71-36-3 (U.S. Environmental Protection Agency, 2010b):
Listed as: 1-Butanol P or U series number: U031 Footnote: Listed as: n-Butyl alcohol P or U series number: U031 Footnote: Editor's Note: The D, F, and K series waste numbers and Appendix VIII to Part 261 -- Hazardous Constituents were not included. Please refer to 40 CFR Part 261.
- EPA SARA Title III, Extremely Hazardous Substance List for CAS71-36-3 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS71-36-3 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: n-Butyl alcohol 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 CAS71-36-3 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS71-36-3 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1120 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1120 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS71-36-3 (NFPA, 2002):
Listed as: Butyl Alcohol Hazard Ratings: Health Rating (Blue): 2 Flammability Rating (Red): 3 (3) Flammable. Liquids and solids that can be ignited under almost all ambient temperature conditions. Including liquids with a flash point below 73 degrees F and a boiling point above 100 degrees F, solid materials which form coarse dusts that burn rapidly without becoming explosive, materials which burn rapidly by reason of self-contained oxygen (ie, organic peroxides), and materials which ignite spontaneously when exposed to air.
Instability Rating (Yellow): 0 Oxidizer/Water-Reactive Designation: Not Listed
-HANDLING AND STORAGE
SUMMARY
Butanol is moderately toxic through skin contact and is a severe skin and eye irritant. Wear appropriate protective clothing including gloves and eye protection when handling butanol. Wash skin thoroughly if it comes in contact with butanol. Butanol is also a flammable liquid; remove clothing promptly if it becomes wet to avoid fire hazard (Lewis, 1996; Sittig, 1991).
HANDLING
- Wear appropriate protective clothing including gloves and eye protection when handling butanol. Ideally, use spark-resistant tools when working around butanol (ITI, 1995; Sittig, 1991).
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Butanol should be stored in a cool, dry, unlighted place away from ignition sources (ITI, 1995; Sittig, 1991). Material should be kept away from explosives, oxidizing materials, organic peroxides, poisons and radioactive materials (ITI, 1995). Spark-resistant construction electrical equipment should be used (ITI, 1995).
Butanol is incompatible with strong oxidizers, strong acids, halogens, caustics, alkali metals, aliphatic amines, and isocyanates (Lewis, 1996; Pohanish & Greene, 1997; Sittig, 1991).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- Contact lenses should not be worn when working with n-butanol (NIOSH , 2000).
Broken packages containing this chemical should not be handled unless appropriate personal protection clothing is worn (AAR, 1998). Butanol is moderately toxic through skin contact and is a severe skin and eye irritant. Wear appropriate protective clothing including gloves and eye protection when handling butanol. Wash skin thoroughly if it comes in contact with butanol. Butanol is also a flammable liquid; remove clothing promptly if it becomes wet to avoid fire hazard (Lewis, 1996; Sittig, 1991).
EYE/FACE PROTECTION
- Wear appropriate eye protection to prevent injury from splashes or vapors (Sittig, 1991).
RESPIRATORY PROTECTION
- 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 71-36-3.
-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.
This compound is a moderate fire risk. It is not highly reactive and shows no adverse reaction during a fire (AAR, 1998; ITI, 1995). If butanol is on fire or involved in a fire, do not extinguish the fire unless the leak can be stopped. Apply water from as far away as possible; use flooding quantities of water to cool containers. Solid streams of water may be ineffective; use flooding quantities of water as fog. Use alcohol foam, dry chemical or carbon dioxide to extinguish the fire (AAR, 1998; Lewis, 1996; Sittig, 1991). Water should be applied from as far a distance as possible (AAR, 1998)
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS71-36-3 (NFPA, 2002):
Listed as: Butyl Alcohol Flammability Rating: 3 (3) Flammable. Liquids and solids that can be ignited under almost all ambient temperature conditions. Including liquids with a flash point below 73 degrees F and a boiling point above 100 degrees F, solid materials which form coarse dusts that burn rapidly without becoming explosive, materials which burn rapidly by reason of self-contained oxygen (ie, organic peroxides), and materials which ignite spontaneously when exposed to air.
- 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 CAS71-36-3 (NFPA, 2002):
- Moderate fire risk; not highly reactive, no adverse reaction takes place in fire (ITI, 1995).
- Alcohol foam, dry chemical, or carbon dioxide may be used to extinguish fires involving this compound (AAR, 1998; Sittig, 1991).
EXPLOSION HAZARD
- Vapors may explode if ignited in an enclosed area (CHRIS , 2000).
Fire and explosion may occur when butanol comes into contact with strong oxidizers (HSDB, 2004). Butanol is a flammable liquid and is moderately explosive. Keep sparks, flames, and other sources of ignition away from areas where butanol is used, handled, or stored (AAR, 1998; Lewis, 1996).
DUST/VAPOR HAZARD
- Vapor has irritating characteristics: Vapors may cause a slight, temporary smarting of the eyes or respiratory system if present in high concentrations (CHRIS , 2000).
Toxic vapors and gases(such as carbon monoxide) can be released in a fire involving this compound (HSDB, 2004). When heated to decomposition it emits acrid smoke and fumes (Lewis, 1996). Vapors may cause dizziness or suffocation (HSDB, 2004). Butanol vapors cause irritation to the eyes, mucous membranes, and to the skin. Other symptoms of high exposure may include symptoms which appear to be alcohol intoxication such as dizziness, headaches, and drowsiness (CNS depression) (Lewis, 1998; Hathaway et al, 1996; Lewis, 1996; Clayton & Clayton, 1994; Raffle et al, 1994; Snyder, 1992).
REACTIVITY HAZARD
- Toxic vapors and gases (such as carbon monoxide) can be released in a fire involving this compound (HSDB, 2004).
Acrid smoke and fumes are produced when butanol is heated to decomposition (Lewis, 1996). Due to its flash point, butanol forms explosive mixtures with air (Pohanish & Greene, 1997).
- Butanol will attack some forms of plastics, rubber, and coatings (HSDB, 2004; Pohanish & Greene, 1997).
- It will burn with a strongly luminous flame (Budavari, 1996).
- In an enclosed area, vapors may explode if ignited (CHRIS , 2000).
- Butanol, used a solvent in a autoclave preparation at 100 degrees C, severely attacked the aluminum gasket, liberating hydrogen which caused a sharp rise in pressure (Bretherick, 1990).
- Butanol is incompatible with strong oxidizers, strong acids, halogens, caustics, alkali metals, aliphatic amines, and isocyanates (Pohanish & Greene, 1997; Lewis, 1996; Sittig, 1991).
- It may react with aluminum above 49 degrees C (120 degrees F) (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.
- AIHA ERPG Values for CAS71-36-3 (AIHA, 2006):
- DOE TEEL Values for CAS71-36-3 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS71-36-3 (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 CAS71-36-3 (National Institute for Occupational Safety and Health, 2007):
IDLH: 1400 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 butanol is not on fire and is not involved in a fire, keep sparks, flames, and other sources of ignition away from the area. Keep spilled butanol out of water sources and sewers; build dikes to contain the spilled butanol as necessary. Attempt to stop the leak only if it can be done without risk to personnel. Knock down vapors with water spray. Absorb the spill with a non-reactive absorbent material and place in vapor-tight containers for disposal (AAR, 1998; Sittig, 1991). If butanol is spilled on land, dig a pit, pond, lagoon, or other holding area to contain the spill. Stop the surface flow by building dikes of soil, sand bags, foamed polyurethane, or foamed concrete. Absorb spilled butanol with fly ash, cement powder, or commercial sorbents (AAR, 1998). If butanol is spilled on water, use natural barriers or oil spill control booms to limit the travel of the spill. Remove trapped butanol with suction hoses (AAR, 1998). If butanol is spilled in air, use water vapor to knock down the vapors (AAR, 1998).
The reported removal rates in secondary treatment of butanol range from 31%-99% based on data from acclimated semi-continuous and continuous flow conditions (Howard et al, 1991). 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
- Butanol primarily enters the environment as a result of its production and use in industrial processes. It occurs in natural sources such as peppermint oil, some teas, apple aromas, and the bacteria strains Clostridium butylicum, and Clostridium acetobutylicum (Howard, 1990).
ENVIRONMENTAL FATE AND KINETICS
In the atmosphere, butanol is degraded by the reaction with photochemically produced hydroxyl radicals with a rate constant of 6 x 10(-10) cm(3)/molecule sec (Howard, 1990). The reported half life of butanol in the air ranges from 8.8 hours to 87.7 hours (3.7 days) based on the photooxidation half life (Howard et al, 1991). The rate constant for butanol and hydroxyl radicals reaction is 8.3X10(-12) cm(3)/molecules/sec. At an atmospheric hydroxyl radical concentration of 5X10(+5) molecules/cm(3), the half-life is expected to be 46 hours (HSDB, 2004). The half-life of butanol in air is estimated to be 46 hours (HSDB, 2004). In the atmosphere, the half-life for vapor phase reaction for butanol with photochemically generated hydroxyl radicals was estimated to be 46 hours (HSDB, 2004).
SURFACE WATER In water, butanol is removed by biodegradation and by volatilization to some extent. Butanol does not absorb to sediments or suspended particles and it does not significantly bioconcentrate (Howard, 1990). The reported half life of butanol in surface water ranges from 24 hours (1 day) to 168 hours (7 days) based on unacclimated freshwater grab sample data (Howard et al, 1991). In water, n-butanol is expected to biodegrade. Volatilization half-life from a model river (1 m deep, flowing 1m/sec, wind velocity 3 m/sec) is estimated to be 2 days. A volatilization half-life of 29 days is estimated from a model lake (1 m deep, flowing at 0.05 m/sec, wind velocity 0.05 m/sec). (HSDB, 2004). The volatilization of n-butanol to volatilize depends upon the temperature, turbulence, current velocity, wind speed, and the depth of the water bodies (HSDB , 2000). This compound is not expected to strongly bind to suspended sediments (HSDB , 2000). Bioconcentration is not a significant fate process (HSDB, 2004). The rate of the reaction between hydroxyl radicals and n-butanol in water is 2.2X10+9 L/mol sec. Assuming an hydroxyl radical concentration of 1X10-17 M in water, this corresponds to a half-life of about 1 year (HSDB , 2000). The reported photooxidation half life in water ranges from 2602 hours (108 days) to 104,000 hours (11.9 years) based on measured rate data for hydroxyl radicals in aqueous solution (Howard et al, 1991).
GROUND WATER
TERRESTRIAL In soils, butanol is removed by volatilization from the surface, by biodegradation, and by leaching into groundwater (Howard, 1990). The reported half life of butanol in soils range from 24 hours (1 day) to 168 hours (7 days) based on estimated unacclimated aqueous aerobic biodegradation (Howard et al, 1991). A soil sorption coefficient (Koc) of 71.6 was estimated, based on a measured log octanol/water partition coefficient of 0.88 (HSDB , 2000). Based on this Koc n-butanol is expected to be moderately to highly mobile in the soil (HSDB, 2004). In soil, n-butanol is expected to leach to groundwater or to biodegrade. Volatilization from the soil surface is also possible (HSDB, 2004).
ABIOTIC DEGRADATION
- Butanol will volatilize from surface soil and water. Volatilization from water bodies is influenced by temperature, turbulence, water velocity, wind speed, and water depth. Adsorption to sediment or suspended matter is not important. It is mobile in soil, based on an estimated organic carbon partition coefficient (Koc) of 71.6, and will leach to groundwater. Butanol will rapidly degrade in water systems. Biodegradation also occurs in soil. Butanol vapors in the atmosphere degrade by reaction with photochemically produced hydroxyl radicals (HSDB, 2004; OHM/TADS , 2000; Howard, 1990).
BIODEGRADATION
- Butanol is reported to be successfully biodegraded in river water, in batch systems, and with adapted, activated sludge (Howard, 1990).
The reported aerobic half life of butanol ranges from 24 hours (1 day) to 168 hours (7 days) based on unacclimated freshwater grab sample data and aqueous screening test data (Howard et al, 1991). The reported anaerobic half life of butanol ranges from 96 hours (4 days) to 1296 hours (54 days) based on acclimated anaerobic screening test data and aqueous aerobic biodegradation (Howard et al, 1991).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- ECOTOXICITY VALUES (OHM/TADS , 2000):
LC100 - CREEK CHUB: 1400 mg/L for 24H LC100 - GOLDFISH: 20 mg/L for 15-96H LC100 - FISH: 1400 mg/L for 24H LC100 - GOLDFISH: 1000 mg/L for 24H LC100 - GOLDFISH: 250 mg/L for 7-20H LC100 - FISH: 400 mg/L for 1H LC100 - MINNOW: 29 mg/L for 24H
- ECOTOXICITY VALUES (HSDB, 2004):
LC50 - FATHEAD MINNOW (Pimephales promelas): 1730 mg/L for 96H -- (95% confidence limit 1630-1840 mg/L); age 33 days old; water hardness 47.7 mg/L (CaCO3); temp 24.7 deg C; pH 7.64; dissolved oxygen 6.3 mg/L, alkalinity 45.5 mg/L (CaCO3); Static bioassay LC50 - FATHEAD MINNOW (Pimephales promelas): 1950, 1950, 1950, 1950, & 1910 mg/L at 1, 24, 48, 72, & 96H, respectively -- 18 to 22 deg C; static bioassay in Lake Superior water LC50 - FATHEAD MINNOW (Pimephales promelas): 1940, 1940, 1940, 1940, & 1940 mg/L at 1, 24, 48, 72, & 96H, respectively -- 18 to 22 deg C; static bioassay in reconstituted water Toxicity Threshold (Cell Multiplication Inhibition Test) - GREEN ALGAE (Scenedesmus quadricauda): 875 mg/L Toxicity Threshold (Cell Multiplication Inhibition Test) - ALGAE (Microcystis aeruginosa): 100 mg/L Toxicity Threshold (Cell Multiplication Inhibition Test) - PROTOZOA (Uronema parduczi Chatton-Lwoff): 8.0 mg/L Toxicity Threshold (Cell Multiplication Inhibition Test) - PROTOZOA (Entosiphon sulcatum): 55 mg/L Toxic Dose - ALGAE (Chlorella pyrenoidosa): 8,500 mg/L EC50 - FATHEAD MINNOW (Pimephales promelas): 1510 mg/L for 96H -- age 33 days old; water hardness 47.7 mg/L (CaCO3); temp 24.7 deg C; pH 7.64; dissolved oxygen 6.3 mg/L; alkalinity 45.5 mg/L (CaCO3); Static bioassay EC50 - DAPHNID (Daphnia magna): 2337 mg/L for 24H -- lost ability to swim EC50 - DAPHNID (Daphnia magna): 1983 mg/L for 48H -- lost ability to swim
- Dangerous to aquatic life in high concentrations (CHRIS , 1991).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Butanol is a watery, colorless liquid with an alcohol odor (CHRIS , 2000).
harsh fuel oil odor with a banana smell, similar to amyl alcohol (HSDB , 2000) It has a dry, burning, banana-like, or fuel-oil taste (HSDB , 2000). Butanol is a colorless, volatile, highly refractive liquid which burns with a strongly luminous flame. Its odor has been described as like fusel oil but weaker, as rancid, and as vinous (Ashford, 1994; Budavari, 1996; Clayton & Clayton, 1994; Hathaway et al, 1996; Lewis, 1996; Lewis, 1997; Lewis, 1998; Snyder, 1992; Verschueren, 1983).
VAPOR PRESSURE
- 4.4 mmHg (at 20 degrees C) (Verschueren, 1983)
- 5.5 mmHg (at 20 degrees C) (Lewis, 1996; Snyder, 1992)
- 6.5 mmHg (at 25 degrees C) (Clayton & Clayton, 1994; Verschueren, 1983)
- 7.024 mmHg (Howard, 1990)
- 10 mmHg (at 10 degrees C) (Verschueren, 1983)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
LIQUID: 0.80978 (at 20/4 degrees C) (Lewis, 1996) LIQUID: 0.810 (at 20/4 degrees C) (Budavari, 1996; Verschueren, 1983) LIQUID: 0.8109 (at 20/20 degrees C) (Lewis, 1997)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
-89 degrees C (Lewis, 1997a) -90 degrees C(Howard, 1990a)
-89.5 degrees C(Howard, 1990a) -89.9 degrees C(Verschueren, 1983a) -90 degrees C (Ashford, 1994a; Budavari, 1996a; Clayton & Clayton, 1994a)
BOILING POINT
- 117-118 degrees C (Budavari, 1996)
- 117-119 degrees C (Ashford, 1994)
- 117.2 degrees C (Howard, 1990; Snyder, 1992)
- 117.4 degrees C (Lewis, 1996)
- 117.7 degrees C (Lewis, 1997; Verschueren, 1983)
- 118 degrees C (Clayton & Clayton, 1994)
- A solution of 63% butanol and 37% water boils continuously at 92 degrees F (Budavari, 1996).
FLASH POINT
- 37 degrees C (closed cup) (NFPA, 1997)
- 35 degrees C; 95 degrees F (Lewis, 1997)
- 36-38 degrees C (Snyder, 1992)
- 52 degrees C (TCC) (Ashford, 1994)
- 95-100 degrees F (Lewis, 1996)
AUTOIGNITION TEMPERATURE
- 365 degrees C; 689 degrees F (Lewis, 1996; Lewis, 1997)
EXPLOSIVE LIMITS
SOLUBILITY
Butanol is miscible with most organic solvents, including alcohol and ether (Ashford, 1994; Budavari, 1996; Lewis, 1996; Lewis, 1997). >10% in acetone, benzene, ether, and ethanol (Snyder, 1992)
OCTANOL/WATER PARTITION COEFFICIENT
- log Kow = 0.88 (Howard, 1990; Verschueren, 1983)
HENRY'S CONSTANT
- 7.0x10(-6) atm-m(3)/mol (Ehrenfeld et al, 1986)
- 5.57 x 10(-6) atm-m(3)/mole (Howard, 1990)
SPECTRAL CONSTANTS
75 (Prism) (Sadtler Reference Number) (HSDB , 2000) 10,934 (Grating) (Sadtler Reference Number) (HSDB , 2000) 4807 (Coblentz Society Spectral Collection) (HSDB , 2000)
OTHER/PHYSICAL
- LIQUID WATER INTERFACIAL TENSION
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