ETHYL BUTYL KETONE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
ETHYL BUTYL KETONE AETHYLBUTYLKETON (German) BUTYL ETHYL KETONE n-BUTYL ETHYL KETONE EBK EPTAN-3-ONE (Italian) ETHYLBUTYLCETONE (French) ETHYLBUTYLKETON (Dutch) ETILBUTILCHETONE (Italian) HEPTAN-3-ON (Dutch, German) HEPTAN-3-ONE 3-HEPTANONE
IDENTIFIERS
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures.
SYNONYM REFERENCE
- (RTECS, 1995;(Lewis, 1992)ACGIH, 1991
USES/FORMS/SOURCES
Ethyl butyl ketone is used as a solvent for nitrocellulose and polyvinyl resins, paints, and for baked-on or air-dried finish mixtures; as a synthetic resin; and as an intermediate (Lewis, 1993) ITI, 1988). It is also used as a synthetic flavoring ingredient (HSDB , 1995).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Ethyl butyl ketone is a mild to moderate irritant of the skin, eyes, and mucous membranes. It may cause dermatitis, but did not result in skin sensitization in human volunteers.
- Ethyl butyl ketone exposure can cause headache and central nervous system depression leading to coma.
- With very large gavage doses for 14 weeks, ethyl butyl ketone caused peripheral neuropathies (central-peripheral distal axonopathies) in rats. This effect has not been seen in exposed humans.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Inhalation or contact with material may irritate or burn skin and eyes. Fire may produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control may cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. Keep victim warm and quiet. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
FIRST AID EYE EXPOSURE - 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. Where there is evidence of skin irritation, 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. INGESTION EXPOSURE - If this chemical has been swallowed, get medical attention immediately. TARGET ORGANS - Eyes, skin, respiratory system, and 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. Ingestion may result in significant esophageal or gastrointestinal tract irritation or burns, and 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. If bronchospasm and wheezing occur, consider treatment with inhaled sympathomimetic agents. ACUTE LUNG INJURY: Maintain ventilation and oxygenation and evaluate with frequent arterial blood gases and/or pulse oximetry monitoring. Early use of PEEP and mechanical ventilation may be needed.
DERMAL EXPOSURE DECONTAMINATION: Remove contaminated clothing and jewelry and place them in plastic bags. Wash exposed areas with soap and water for 10 to 15 minutes with gentle sponging to avoid skin breakdown. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999). Treat dermal irritation or burns with standard topical therapy. Patients developing dermal hypersensitivity reactions may require treatment with systemic or topical corticosteroids or antihistamines.
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.
INGESTION EXPOSURE Because of the potential for gastrointestinal tract irritation, Do not induce emesis. Significant esophageal or gastrointestinal tract irritation or burns may occur following ingestion. The possible benefit of early removal of some ingested material by cautious gastric lavage must be weighed against potential complications of bleeding or perforation. GASTRIC LAVAGE: Consider after ingestion of a potentially life-threatening amount of poison if it can be performed soon after ingestion (generally within 1 hour). Protect airway by placement in the head down left lateral decubitus position or by endotracheal intubation. Control any seizures first. ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old. Observe patients with ingestion carefully for the possible development of esophageal or gastrointestinal tract irritation or burns. If signs or symptoms of esophageal irritation or burns are present, consider endoscopy to determine the extent of injury.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
One reference states that the lowest published lethal concentration of ethyl butyl ketone for rats (inhalation route) is 2000 ppm/4 hours (RTECS, 1995). Other references state that no rats died during 4-hour exposures of rats to 2000 ppm, while all rats died at 4-hour exposures to 4000 ppm (ACGIH, 1991; (Hathaway et al, 1991; Clayton & Clayton, 1982). A single, 6-hour exposure to 5800 ppm ethyl butyl ketone killed all three rats exposed. Six-hour exposures to 420 and 3000 ppm did not produce death (Clayton & Clayton, 1982). The LD50 for penetration of rabbit skin was greater than 20 mL/kg (Hathaway et al, 1991).
MAXIMUM TOLERATED EXPOSURE
HUMAN - Ethyl butyl ketone (4% in petrolatum) produced no irritation to human skin after 48 hours under an occlusive patch. The same concentration used in maximization tests on 25 volunteers failed to produce sensitization (ACGIH, 1991; (Clayton & Clayton, 1982).
Rats given 1% ethyl butyl ketone in drinking water for 120 days showed no signs of neurotoxicity. Exposure of rats at 700 ppm, 72 hours/week for 24 weeks was also without neurotoxic effect (ACGIH, 1991). Extremely large gavage doses of ethyl butyl ketone, 2 g/kg/day, 5 days/week for 16 weeks were required to produce signs of neurotoxicity. Two of two rats had hind limb weakness and tail drag (ACGIH, 1991). Dropped into rabbit eyes or applied to skin, the liquid has caused mild irritation (Hathaway et al, 1991). Rats and guinea pigs survived 6-hour daily exposures to 400 to 500 ppm for 10 days. Rats survived single, 6-hour exposures to 420 and 3000 ppm (Clayton & Clayton, 1982).
- Carcinogenicity Ratings for CAS106-35-4 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Ethyl butyl ketone EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Ethyl butyl ketone 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 CAS106-35-4 (U.S. Environmental Protection Agency, 2011):
References: RTECS, 1994 LCLo- (INHALATION)RAT: LD50- (SKIN)RABBIT: LD50- (ORAL)RAT:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS106-35-4 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
- AIHA WEEL Values for CAS106-35-4 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS106-35-4 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS106-35-4 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS106-35-4 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS106-35-4 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS106-35-4 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS106-35-4 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS106-35-4 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS106-35-4 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS106-35-4 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS106-35-4 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions (49 CFR 172.101, 2005):
- ICAO International Shipping Name (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS106-35-4 (NFPA, 2002):
-HANDLING AND STORAGE
HANDLING
- Before heat is applied for the purpose of welding or cutting a vessel that has contained ketones, including ethyl butyl ketone, the vessel should be emptied and purged to remove every trace of flammable material (HSDB, 1994).
STORAGE
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- Use of appropriate protective equipment and good industrial hygiene practices should preclude injury to the skin and eyes. The low volatility of ethyl butyl ketone should prevent injury due to inhalation of the vapors (HSDB , 1995).
- Wear appropriate personal protective clothing to prevent skin contact. Wear appropriate eye protection to prevent eye contact. The worker should immediately wash the skin when it becomes contaminated. Work clothing that becomes wet or significantly contaminated should be removed and replaced (NIOSH, 1995).
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 106-35-4.
-PHYSICAL HAZARDS
FIRE HAZARD
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures. POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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.
Ethyl butyl ketone is a combustible liquid (Lewis, 1992). It is a moderate fire hazard (ACGIH, 1991). The problem of flammability for ethyl butyl ketone should not be significant unless it is handled at elevated temperatures(HSDB, 2004) .
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS106-35-4 (NFPA, 2002):
- INITIATING OR CONTRIBUTING PROPERTIES
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Water spray, fog or alcohol-resistant foam. Use water spray or fog; 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 127 (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 CAS106-35-4 (NFPA, 2002):
- To fight fire, use foam, carbon dioxide, or dry chemical (Lewis, 1992).
- Use water to keep fire-exposed containers cool. If leak or spill has not ignited, use water spray to disperse vapors and to provide protection for personnel attempting to stop the leak or spill. Water spray may be used to flush spills away from exposures (HSDB, 2004).
EXPLOSION HAZARD
- Ethyl butyl ketone should not be allowed to enter a confined space, such as a sewer, because of the possibility of explosion(HSDB, 2004).
Ethyl butyl ketone is incompatible and highly reactive with oxidizers, acetaldehyde, and perchloric acid (HSDB, 2004). The condensation reaction of acetaldehyde with ketones can be violent (HSDB, 2004). Ketones undergo violent decomposition in contact with 68 to 72% perchloric acid (HSDB, 1994).
REACTIVITY HAZARD
- Ethyl butyl ketone can react with oxidizing materials (Lewis, 1992).
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 127 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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 127 (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 CAS106-35-4 (AIHA, 2006):
- DOE TEEL Values for CAS106-35-4 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Ethyl butyl ketone (3-Heptanone) TEEL-0 (units = ppm): 50 TEEL-1 (units = ppm): 75 TEEL-2 (units = ppm): 200 TEEL-3 (units = ppm): 1,000 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 CAS106-35-4 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS106-35-4 (National Institute for Occupational Safety and Health, 2007):
IDLH: 1000 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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 127 (ERG, 2004)
A 3.7 percent theoretical biochemical oxygen demand (BOD) was observed for ethyl butyl ketone (initial concentration of 500 ppm) in a Warburg respirometer after 1 day of incubation with activated sludge inocula at 20 degrees C (HSDB, 2004). 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.
Large quantities can be collected and atomized in a suitable combustion chamber equipped with an appropriate effluent gas cleaning device(HSDB, 2004) . Ethyl butyl ketone may also be disposed of by absorbing in vermiculite, dry sand, or earth, and disposing in a secured sanitary landfill (HSDB, 2004).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Ethyl butyl ketone is released in emissions from forests and diesel engines. It may be released to the environment in effluents from waste treatment facilities and textile finishing plants. It is a volatile constituent of beef flavor (HSDB, 2004).
ENVIRONMENTAL FATE AND KINETICS
If released to the atmosphere, ethyl butyl ketone is expected to exist almost entirely in the vapor phase. Vapor phase ethyl butyl ketone is expected to readily degrade by reaction with photochemically produced hydroxyl radicals with an estimated half-life of 2 days (HSDB, 2004). The rate constant for the vapor phase reaction of ethyl butyl ketone with photochemically produced hydroxyl radicals can be estimated from a structure activity relationship to be 8.1 x 10(-12) cm(3)/molecule-sec at 25 degrees C, which corresponds to an atmospheric half-life of about 2 days at an atmospheric concentration of 5 x 10(+5) hydroxyl radicals per cm(3). Heptanones are generally resistant to hydrolysis and, therefore, ethyl butyl ketone (3-heptanone) would not be expected to hydrolyze in the environment (HSDB, 2004).
SURFACE WATER Volatilization half-lives of 13 hours and 7 days have been estimated for a model river (1 meter deep) and a model lake (1 meter deep), respectively. Estimated Koc values of 44 and 25 and a BCF of 6 suggest that adsorption to sediment and bioconcentration in aquatic organisms will not be important. Hydrolysis in water is not likely to be important due to a lack of hydrolyzable groups. Insufficient data are available to fully assess the importance of biodegradation in water (HSDB, 2004).
TERRESTRIAL Estimated Koc values of 44 and 25 indicate high mobility in soil and low adsorption potential for ethyl butyl ketone. An experimental vapor pressure of 2.6 mmHg at 20 degrees C suggests that volatilization from dry soil surfaces may be important. Insufficient data are available to fully assess the importance of biodegradation in soil (HSDB, 2004).
ABIOTIC DEGRADATION
- Ethyl butyl ketone vapor reacts with photochemically produced hydroxyl radicals in the atmosphere. Hydrolysis is not expected in the environment. High mobility in soil and low adsorption potential to soil or sediment are likely, based on the organic carbon partition coefficients (Koc's) of 44 and 25. It will volatilize from water and possibly from dry soil surfaces, based on an experimental vapor pressure of 2.6 mmHg at 20 degrees C (HSDB, 2004).
BIODEGRADATION
- One screening study suggested that biodegradation in soil and water may be slow; however, the initial concentration of ethyl butyl ketone was high and may have been toxic to microorganisms. Insufficient data are available to fully assess the importance of biodegradation in soil and water (HSDB, 2004).
BIOACCUMULATION
Based on an experimental water solubility of 4300 at 20 degrees C and a recommended regression derived equation, the BCF for ethyl butyl ketone can be estimated to be about 6. This BCF value indicates that bioconcentration in aquatic organisms will not be an important fate process (HSDB, 2004).
ENVIRONMENTAL TOXICITY
- No information found at the time of this review.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
- 114.21 (Lewis, 1992; RTECS , 1994)
DESCRIPTION/PHYSICAL STATE
- Ethyl butyl ketone is a clear, colorless, mobile, flammable liquid with a fatty or strong fruity odor and a melon or banana flavor (Lewis, 1992) ACGIH, 1991; (Clayton & Clayton, 1982) HSDB, 1994).
PH
VAPOR PRESSURE
- 1.4 mmHg (at 25 degrees C) (ACGIH, 1991)
- 2.6 mmHg (at 20 degrees C) (experimental) (HSDB, 1994)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
BOILING POINT
- 148 degrees C (Lewis, 1992)
FLASH POINT
- 46.11 degrees C; 115 degrees F (open cup) (Lewis, 1992) ACGIH, 1991)
- 37 degrees C; 98.6 degrees F (closed cup) (ACGIH, 1991)
EXPLOSIVE LIMITS
SOLUBILITY
Ethyl butyl ketone is insoluble in water (ACGIH, 1991). It is miscible with water at 149 degrees C (Lewis, 1992).
Ethyl butyl ketone is miscible with alcohol and ether degrees C (Lewis, 1992). Other references state that ethyl butyl ketone is soluble in alcohol (ACGIH, 1991; (Lewis, 1993) and other organic solvents (ACGIH, 1991).
HENRY'S CONSTANT
- 9.1x10(-5) atm-m(3)/mol (at 20 degrees C) (estimated) (HSDB, 1994)
SPECTRAL CONSTANTS
-REFERENCES
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