ETHYL ETHER
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
AETHER ANAESTHETIC ETHER ANESTHESIA ETHER ANESTHETIC ETHER DIAETHYLAETHER (German) DIETHYL ETHER DIETHYL OXIDE DWUETYLOWY ETER (Polish) ETERE ETILICO (Italian) ETHANE, 1,1'-OXYBIS- ETHER ETHER, ETHYL ETHER ETHYLIQUE (French) ETHOXYETHANE ETHYL ETHER ETHYL OXIDE 3-OXAPENTANE 1,1'-OXYBISETHANE OXYDE D'ETHYLE (French) PRONARCOL SOLVENT ETHER 3-OXYPENTANE
IDENTIFIERS
1155-Ethyl ether 1155-Diethyl ether
SYNONYM REFERENCE
- (HSDB , 1999; RTECS , 1999)
USES/FORMS/SOURCES
Ethyl ether is used as a diesel fuel ignition primer, a smokeless powder, an extractant, and as an industrial solvent for waxes, fats, oils, perfumes, alkaloids, and gums. It is an important reagent in organic syntheses and analytic chemistry, especially in Grignard/Wurtz reactions. It was formerly used as an anesthetic gas (ACGIH, 1991; Ashford, 1994; Harbison, 1998; Hathaway et al, 1996; Lewis, 1997; Lewis, 1998).
Ethyl ether is a colorless, very volatile, mobile, hygroscopic liquid (below 34 degrees C (94 degrees F)) with a pungent, aromatic odor and a burning and sweet taste. It is available in ACS Reagent, ACS Absolute, CP, concentrated, USP 1880, USP (anesthesia), washed, motor, and electronic grades (AAR, 1998; (ACGIH, 1991; Ashford, 1994; Budavari, 1996; Harbison, 1998; ILO, 1998; Lewis, 1996; Lewis, 1997; Lewis, 1998) NFPA, 1994; (Verschueren, 1983). The USP formulation contains 3% ethanol and is marketed in sealed containers with copper liners to retard oxidation.
Ethyl ether is produced by dehydration of ethanol and catalytic hydration of ethylene (Ashford, 1994; Budavari, 1996; Lewis, 1997).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Ingestion poisonings are similar to ethanol overdoses except for a more rapid onset and shorter duration of symptoms. Inhalation may result in dizziness, giddiness, euphoria, and CNS depression. Deliberate abuse has been reported with repeated exposures producing ether jags. Deaths from acute industrial exposure are rare. Death due to respiratory depression may result from severe and continued exposure.
- Ethyl ether is a severe eye and moderate skin irritant.
- 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.
ACUTE CLINICAL EFFECTS
- Ether can cause slight, reversible eye injury from contact with the liquid or vapor. It is rapidly absorbed through the lungs, but is not appreciably absorbed through intact skin (Clayton & Clayton, 1982).
- Its main effects are NARCOSIS, ANESTHESIA, and CNS depression. Inhalation of an airborne concentration of 200 ppm may produce some nasal irritation. An airborne concentration of 1.9 volume percent can cause anesthesia, 7 to 10 vol percent may cause respiratory arrest, and concentrations greater than 10 percent are fatal (Clayton & Clayton, 1982; (ACGIH, 1986) if artificial respiration is not provided.
- Effects of of acute ether exposure include excitement, drowsiness, vomiting, paleness, decreased pulse and temperature, irregular respiration, excessive salivation, muscle relaxation, possible kidney injury, kidney irritation, and temporarily abnormal liver function tests (Clayton & Clayton, 1982).
- Coughing, bronchodilation, increase in respiratory and heart rates, cardiac arrhythmias (rarely), hyperglycemia (HSDB), and loss of memory (Adam, 1973) have also been reported from acute exposures, some in the anesthetic range.
- Ethyl ether is a potential drug of abuse, mainly by inhalation. Acute respiratory distress syndrome (ARDS) was described in a woman who used ether recreationally by intravenous injection. Florid pneumonitis ensued, with bilateral pulmonary edema (Lambermont et al, 1998).
- Ether is taken up by the brain and body fat (HSDB, 2000). It was previously used as a bronchodilator to treat acute asthma attacks (Robertson, 1985).
CHRONIC CLINICAL EFFECTS
- Humans develop a TOLERANCE to ether upon repeated exposures. There have been few cases of industrial overexposure (ILO, 1983). Generally, ether is well controlled in the workplace because of its fire hazard.
- Prolonged or repeated direct skin contact can produce defatting dermatitis with dryness and cracking (ACGIH, 1986). Other symptoms of chronic exposure include nasal irritation, loss of appetite, headache, sleepiness, dizziness, excitement, personality changes (ILO, 1983; ACGIH, 1986), and excessive sweating (HSDB). Albuminuria and polycythemia have rarely been reported (ACGIH, 1986).
- Rats exposed to airborne concentrations of 0.02 to 2% of ether for 30 weeks had altered liver function enzymes (Collins, 1978).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
-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 - Promptly wash the contaminated skin with water. If this chemical penetrates the clothing, promptly remove the clothing and wash the skin with water. 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, and central nervous system (National Institute for Occupational Safety and Health, 2007).
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 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. ACTIVATED CHARCOAL
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
There is little data on deaths resulting from exposure to ethyl ether. Humans generally refrain from ingesting ethyl ether due to its irritating effect on mucous membranes; however, deaths have been reported following the intentional ingestion of as little as 30 mL of liquid ethyl ether. (Bingham et al, 2001; Baselt, 2000; Baselt & Cravey, 1995).
MAXIMUM TOLERATED EXPOSURE
Ethyl ether is quickly absorbed through the lungs and the primary result is CNS depression and anesthesia. However, there is a wide range of concentrations between nasal irritation (200 ppm) and more serious health hazards (100,000- 150,000 ppm) which may include respiratory arrest. Exposure to liquid or high concentrations of vapor ethyl ether causes eye and mucous membrane irritation. Brief skin exposure to ethyl ether has no effect; repeated skin exposures causes drying and cracking (Bingham et al, 2001; Baselt, 2000; ACGIH, 1991; Baselt & Cravey, 1995; Hathaway et al, 1996; Zenz, 1994). Industrial exposures of 500-1000 ppm did not result in demonstrable injury to health and concentrations of up to 7000 ppm have been tolerated, but a 500 ppm limit seems appropriate to avoid irritation (ACGIH, 1991; Hathaway et al, 1996; Zenz, 1994). Early symptoms of acute inhalation overexposure include excitement or drowsiness, vomiting, paleness, lowered pulse and body temperature, irregular respiration, muscular relaxations, and excessive salivation. Temporary aftereffects of acute exposure include vomiting, salivation, respiratory passage irritation, headaches, and depression or excitation (Bingham et al, 2001; Baselt, 2000; Baselt & Cravey, 1995; Harbison, 1998; Hathaway et al, 1996; Lewis, 1998; Zenz, 1994). A degree of tolerance may be acquired from repeated exposures to ethyl ether. Symptoms resulting from chronic inhalation exposure include loss of appetite, exhaustion, headache, sleepiness, dizziness, excitation, and psychic disturbances; albuminuria and polycythemia may result (Baselt, 2000; ACGIH, 1991; Baselt & Cravey, 1995; Harbison, 1998; Hathaway et al, 1996; Zenz, 1994).
- Carcinogenicity Ratings for CAS60-29-7 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Ethyl ether EPA (U.S. Environmental Protection Agency, 2011): Not Assessed under the IRIS program. ; Listed as: Ethyl ether 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 ether 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 CAS60-29-7 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 2x10(-1) mg/kg-day
Inhalation: Drinking Water:
CALCULATIONS
1 ppm = 3.03 mg/m(3) (Verschueren, 1983) 1 mg/m(3) = 0.330 ppm (Verschueren, 1983)
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS60-29-7 (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 CAS60-29-7 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS60-29-7 (National Institute for Occupational Safety and Health, 2007):
Listed as: Ethyl ether REL: IDLH: IDLH: 1900 ppm Note(s): [10%LEL]
- OSHA PEL Values for CAS60-29-7 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS60-29-7 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS60-29-7 (U.S. Environmental Protection Agency, 2010):
Listed as: Ethyl ether 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: Ethane, 1,1[prime]-oxybis- Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Ethyl ether Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS60-29-7 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS60-29-7 (U.S. Environmental Protection Agency, 2010b):
Listed as: Ethane, 1,1[prime]-oxybis- P or U series number: U117 Footnote: Listed as: Ethyl ether P or U series number: U117 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 CAS60-29-7 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS60-29-7 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS60-29-7 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS60-29-7 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1155 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1155 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS60-29-7 (NFPA, 2002):
Listed as: Ethyl Ether Hazard Ratings: Health Rating (Blue): 1 Flammability Rating (Red): 4 (4) Extremely flammable. Materials which will rapidly vaporize at normal pressure and temperature and will burn readily. Including: gases, cryogenic materials, any liquid or gaseous material having a flash point below 73 degrees F and a boiling point below 100 degrees F, and materials which can form explosive mixtures with air.
Instability Rating (Yellow): 1 (1) Materials which are normally stable, but which can become unstable at elevated temperatures and pressures, or which may react with water with some release of energy, but not violently.
Oxidizer/Water-Reactive Designation: Not Listed
-HANDLING AND STORAGE
SUMMARY
Ethyl ether is mildly toxic by inhalation and moderately toxic by ingestion; however, it must not be considered safe to inhale or ingest. It is a severe eye and a moderate skin irritant. When inhaled, ethyl ether causes CNS depression and produces headache, intoxication, drowsiness, stupor, and unconsciousness. Respiratory failure from severe and continued exposure to ethyl ether may result in death (Clayton & Clayton, 1993; Harbison, 1998; ILO, 1998; Lewis, 1996). Ethyl ether presents an extremely dangerous fire and explosion hazard when exposed to heat or flame. It is a storage hazard and must be inhibited with ferrous sulfate to avoid the formation of explosive peroxides. In areas in which ethyl ether is manufactured, handled, or stored, explosion-proof electrical equipment and fittings should be used and sources of ignition (e.g. smoking or open flames) should be prohibited (ACGIH, 1991; Budavari, 1996; Harbison, 1998; ITI, 1995; Lewis, 1996; Sittig, 1991).
HANDLING
- Use only non-sparking tools and equipment, especially when opening and closing containers (Sittig, 1991).
STORAGE
Ethyl ether should be stored in tightly-closed containers; bottles, cans, and drums are among the typical shipping containers for this compounds. Ground and bond metal containers when they involve the transfer of 5 gallons or more, and equip drums with self-closing valves, flame arresters, and pressure vacuum bungs (NFPA, 1997; Sittig, 1991).
- ROOM/CABINET RECOMMENDATIONS
Containers of ethyl ether should be stored in cool, dry, well-ventilated areas away from heat and sunlight. Protect containers from damage, static electricity, and lightning. A standard flammable liquid storage room should be used for indoor storage, though outdoor detached storage is preferred (ITI, 1995; NFPA, 1997; Sittig, 1991).
Ethyl ether forms explosive mixtures with air. It is incompatible with strong acids and strong oxidizers. It can form explosive peroxides with air and light. Ethyl ether attacks some plastics, rubber, and coatings. It can accumulate static electric charges that may cause explosion (ACGIH, 1991; Pohanish & Greene, 1997; NFPA, 1997; Sittig, 1991).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- Mildly toxic by inhalation and moderately toxic by ingestion, ethyl ether is a severe eye and a moderate skin irritant. Breathing the vapors should be avoided. This compound presents an extremely dangerous fire and explosion hazard if exposed to heat or flame. Protective clothing, including a positive pressure self-contained breathing apparatus, should be worn to avoid repeated or pronlonged contact, and broken containers should not be handled unless wearing suitable clothing. To avoid a flammability hazard, clothing should be immediately removed when it becomes wet or contaminated. Use copious amounts of water or of soap and water to wash away ethyl ether that may have come in contact with the body (AAR, 1998; (Lewis, 1996; NFPA, 1997; Sittig, 1991).
EYE/FACE PROTECTION
- Eye protection should be worn to prevent the reasonable probability of eye contact (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 60-29-7.
-PHYSICAL HAZARDS
FIRE HAZARD
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 ether is a flammable liquid and presents an extremely dangerous fire and explosion hazard when exposed to heat or flame. The vapors are heavier than air and may travel to a source of ignition and flash back. Liquid ethyl ether floats on water and may travel to a source of ignition and spread a fire. The vapors, which are heavier than air, may travel to a source of ignition and cause a flashback. Liquid ethyl ether may cause a fire to spread since it floats on water and may travel to a source of ignition. It can accumulate static electricity as a result of flow or agitation (AAR, 1998; (ILO, 1998; ITI, 1995; Lewis, 1996; NFPA, 1997; Sittig, 1991).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS60-29-7 (NFPA, 2002):
Listed as: Ethyl Ether Flammability Rating: 4 (4) Extremely flammable. Materials which will rapidly vaporize at normal pressure and temperature and will burn readily. Including: gases, cryogenic materials, any liquid or gaseous material having a flash point below 73 degrees F and a boiling point below 100 degrees F, and materials which can form explosive mixtures with air.
- 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 CAS60-29-7 (NFPA, 2002):
- If ethyl ether is on fire or involved in a fire, do not extinguish the fire unless the flow of ethyl ether can be stopped. Water may be ineffective. Use water in flooding quantities to keep fire-exposed containers cool; apply water from as far away as possible. Solid streams of water may spread the fire. Use foam, dry chemical, or carbon dioxide to fight fire (AAR, 1998; (Lewis, 1996; NFPA, 1997; Sittig, 1991).
The phrase "water may be ineffective" indicates that, although water can be used to cool and protect exposed material, water may not be capable of extinguishing the fire unless used under favorable conditions by experienced fire fighters trained in fighting all types of flammable liquid fires (NFPA, 1997). Alcohol-resistant fire fighting foam is recommended for use on all water-soluble liquids or polar solvent-type liquids, except for those that are only "very slightly" soluble. Certain judgement factors are introduced, however, since ordinary fire fighting foam may be used on some liquids that are only "slightly" soluble, particularly if the foam is applied at higher-than-normal application rates. Conversely, some flammable liquids, such as the higher molecular weight alcohols and amines, will destroy alcohol-resistant foams, even when applied at very high rates. Foams should not be used on water-reactive materials (NFPA, 1997).
EXPLOSION HAZARD
- Ethyl ether is a very dangerous explosion hazard when exposed to heat or flame. It can form explosive peroxides when exposed to light or air, or when stored for longer than six months. It reacts violently with oxidizers (ITI, 1995; ILO, 1998; Lewis, 1996; NFPA, 1997).
- Ethyl ether auto-oxidizes to form explosive polymeric 1-oxyperoxides (Lewis, 1996).
The hydroperoxide initially formed by autoxidation of ether is not particularly explosive, but after standing and evaporation, polymeric 1-oxyperoxides are formed which are dangerously explosive, even below 100 degrees C (Urben, 1995).
- Ethyl ether forms explosive mixtures with air. It can also form unstable peroxides when exposed to light or air (ILO, 1998; ITI, 1995; Lewis, 1996; Pohanish & Greene, 1997).
Ethyl ether tends to form explosive peroxides when exposed to air and light, especially when evaporation to dryness is attempted. Remove peroxides from ethyl ether by shaking with a 5% aqueous ferrous sulfate solution. The addition of naphthols, polyphenols, aromatic amines, and aminophenols has been proposed for the stabilization of ethyl ether (Budavari, 1996). "Peroxide formation may occur in containers that have been opened and remain in storage for more than six months. Peroxides can be detonated by friction, impact, or heating" (NFPA, 1997).
- Ethyl ether forms an explosive reaction with (Lewis, 1996; Urben, 1995):
- Refer to the REACTIVITY HAZARD section for more information on violent and vigorous reactions.
DUST/VAPOR HAZARD
- Ethyl ether vapors are heavier than air and may travel along the ground to a source of ignition and flash back (AAR, 1998; (ILO, 1998; NFPA, 1997).
- When heated to decomposition, ethyl ether emits acrid smoke and irritating fumes (Lewis, 1996).
REACTIVITY HAZARD
- Ethyl ether auto-oxidizes to form explosive polymeric 1-oxyperoxides (Lewis, 1996).
The hydroperoxide initially formed by autoxidation of ether is not particularly explosive, but after standing and evaporation, polymeric 1-oxyperoxides are formed which are dangerously explosive, even below 100 degrees C (Urben, 1995).
- Ethyl ether forms explosive mixtures with air. It can also form unstable peroxides when exposed to light or air (ILO, 1998; ITI, 1995; Lewis, 1996; Pohanish & Greene, 1997).
Ethyl ether tends to form explosive peroxides when exposed to air and light, especially when evaporation to dryness is attempted. Remove peroxides from ethyl ether by shaking with a 5% aqueous ferrous sulfate solution. The addition of naphthols, polyphenols, aromatic amines, and aminophenols has been proposed for the stabilization of ethyl ether (Budavari, 1996). "Peroxide formation may occur in containers that have been opened and remain in storage for more than six months. Peroxides can be detonated by friction, impact, or heating" (NFPA, 1997).
- Ethyl ether is incompatible with strong acids and strong oxidizers (ITI, 1995; ILO, 1998; Pohanish & Greene, 1997).
It forms an explosive reaction with (Lewis, 1996; Urben, 1995): Ethyl ether forms a violent reaction or ignites on contact with (ITI, 1995; Lewis, 1996; Urben, 1995): halogens (eg, bromine, chlorine) interhalogens (eg, iodine heptafluoride) oxidants (eg, chromyl chloride, fluorine nitrate, hydrogen peroxide, iodine(VII) oxide, liquid air, nitric acid, nitrosyl perchlorate, nitryl perchlorate, ozone, permanganic acid, peroxodisulfuric acid, silver perchlorate, sodium peroxide) sulfur and sulfur compounds (eg, sulfur when dried with peroxidized ether, sulfuryl chloride)
Ethyl ether can react vigorously with (ITI, 1995; Lewis, 1996; Urben, 1995):
- Some plastics, rubber and coatings may be attacked by ethyl ether (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 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.
- If a fire involving ethyl ether becomes uncontrollable, or if containers are exposed to direct flame, consider evacuating a one-third mile radius (AAR, 1998).
- If ethyl ether is leaking and not on fire, consider an evacuation of the downwind areas based on the amount of ethyl ether spilled, the location of the spill, and the weather conditions (AAR, 1998).
- AIHA ERPG Values for CAS60-29-7 (AIHA, 2006):
- DOE TEEL Values for CAS60-29-7 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Ethyl ether TEEL-0 (units = ppm): 400 TEEL-1 (units = ppm): 500 TEEL-2 (units = ppm): 500 TEEL-3 (units = ppm): 1,900 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 CAS60-29-7 (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 CAS60-29-7 (National Institute for Occupational Safety and Health, 2007):
IDLH: 1900 ppm Note(s): [10%LEL]
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) If ethyl ether is not on fire and not involved in a fire, keep sparks, flames, and other sources of ignition away from the area; ventilate the area. Restrict persons not wearing appropriate protective clothing from the spill area until cleanup is complete. Attempt to stop the leak if this can be done without undue risk. Absorb spilled ethyl ether in vermiculite, dry sand, earth, or a similar material and deposit in sealed containers. Use water spray to cool and disperse vapors and to dilute spills to form nonflammable mixtures. Keep ethyl ether out of water sources; build dikes to contain flow as necessary. Keep it out of sewers to avoid the possibility of explosion. Control runoff and isolate discharged material for proper disposal (AAR, 1998; (NFPA, 1997; Sittig, 1991).
Ethyl ether little to no biodegradation was observed in short-term screening tests using sewage sludge inocula or soil inocula (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.
Discharge concentrated liquid waste containing no peroxides at a controlled rate near a pilot flame (Sittig, 1991). Perforate a container of concentrated liquid waste containing peroxides from a safe distance and follow with an open burn (Sittig, 1991). Dissolve ethyl ether in benzene, petroleum ether, or butanol and then burn the solution (ITI, 1995).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Ethyl ether may be released to the environment as a result of its industrial uses, especially its use as a solvent and as a primer for gasoline engines, and in manufacturing waste streams (HSDB, 2004; Howard, 1993).
- The general population may be exposed to ethyl ether in drinking water and ambient air; it has been detected, but not quantified, in drinking water, groundwater, and air samples collected from sites across the United States. It is also a component of some household products (HSDB, 2004).
ENVIRONMENTAL FATE AND KINETICS
If ethyl ether is released into the atmosphere, it will exist almost entirely in the vapor phase. It degrades in the atmosphere through photooxidation reaction with photochemically-produced hydroxyl radicals. Direct photolysis is not an important removal process since ethyl ether does not absorb light at wavelengths >290 nm. Atmospheric washout is possible due to its high water solubility (HSDB, 2004; Howard, 1993). The rate constant for the vapor-phase reaction of ethyl ether with photochemically-produced hydroxyl radicals has been measured as 1.34x10(-11) cm(3)/molecule-sec at 25 degrees C, which corresponds to an atmospheric half-life of 29 hours at an atmospheric concentration of 5x10(5) hydroxyl radicals/cm(3) (Howard, 1993). Half-lives for ethyl ether's reaction with hydroxyl radicals and nitrate radicals in the atmosphere have been estimated to be 1.2 days (rate constant = 1.31 x 10(-11) cm(3)/molecule-sec and 5 x 10(5) hydroxyl radicals/cm(3)) and 5.8 days (rate constant = 2.80 x 10(-15) mc(3)/molecule-sec and 5 x 10(8) nitrate radicals/cm(3)), respectively (HSDB, 2004).
SURFACE WATER Reaction of ethyl ether with photochemically-produced hydroxyl radicals in water should not be an important fate process based on a half-life of 204 days (calculated from a measured rate constant of 3.9x10(9) L/mol-sec). Ethers are generally resistant to aqueous environmental hydrolysis, therefore, hydrolysis is not expected to be significant under normal environmental conditions (pH 5-9). Direct photolysis will not be an important removal process, as ethyl ether does not absorb light at wavelengths >290 nm (HSDB, 2004; Howard, 1993). In surface waters, ethyl ether volatilizes quickly. Aqueous hydrolysis is not an important removal process. Ethyl ether does not directly photolyze or significantly photooxidize (HSDB, 2004; Howard, 1993). Estimated volatilization half-lives for ethyl ether from a model river (1 m deep, flowing 1 m/sec, wind velocity 3 m/sec) and a model lake (1 m deep, flowing 0.05 m/sec, wind velocity 3 m/sec) are 3.1 hours and 3.6 days, respectively (HSDB, 2004). Half-life of ethyl ether volatilization from pond water was calculated at ~36 hours at 25 degrees C (Verschueren, 2001).
Ethyl ether is not expected to adsorb to suspended solids or sediment in the water column or to bioconcentrate in aquatic organisms (HSDB, 2004).
TERRESTRIAL Ethyl ether volatilizes quickly from both moist and dry soil and terrestrial surfaces. It is highly mobile in soil and is subject to significant leaching. It does not chemically hydrolyze in soil and is relatively resistant to biodegradation (HSDB, 2004; Howard, 1993).
ABIOTIC DEGRADATION
- If released to the atmosphere, ethyl ether is expected to exist solely as a vapor, based on its vapor pressure of 538 mmHg at 25 degrees C. Vapor phase ethyl ether will be degraded through reaction with photochemically-produced hydroxyl radicals and nitrate radicals. Direct photolysis is not expected to occur (HSDB, 2004).
- On land, ethyl ether is expected to have high mobility in soils. Volatilization from both moist and dry soil surfaces is also expected, based on a Henry's Law contact of 1.23 x 10(-3) atm-m(3)/mole and its vapor pressure of 538 mmHg at 25 degrees C (HSDB, 2004).
- If released to water, ethyl ether is expected to volatilize from water surfaces. Adsorption to suspended solids and sediments and bioconcentration in aquatic organisms are not expected (HSDB, 2004).
BIODEGRADATION
- Based on results from screening tests using sewage sludge inocula and soil inocula, ethyl ether is not expected to be subject to rapid or significant biodegradation (HSDB, 2004; Howard, 1993).
BIOACCUMULATION
The bioconcentration factor (BCF) for ethyl ether is estimated to be 2.8 based on the log octanol-water partition coefficient and 1.3 based on the water solubility. These BCF values suggest that ethyl ether does not significantly bioconcentrate in aquatic organisms (Howard, 1993). Ethyl ether BCFs of 0.9 to 1.4 (at 500 mcg/L initial concentration) and <1.7 to 9.1 (at 50 mcg/L initial concentration) were measured in carp. Based on these numbers, bioconcentration is expected to be low (HSDB, 2004).
ENVIRONMENTAL TOXICITY
LC0 - BLUEGILL (Lepomis macrochirus): >10,000 mg/L for 24-96H -- static bioassay (Verschueren, 2001) LC0 - INLAND SILVERSIDE (Menidia beryllina): >10,000 mg/L for 24-96H -- static bioassay (Verschueren, 2001) LC50 - FATHEAD MINNOW (Pimephales promelas): 2560 mg/L for 96H -- conditions of bioassay not specified (HSDB, 2004) LC50 - FATHEAD MINNOW (Pimephales promelas): 2600 mg/L for 96H (Verschueren, 2001) LC50 - GOLDEN ORFE: 2800 mg/L for 48H (Verschueren, 2001) LC50 - GUPPY (Poecilia reticulata): 2138 mg/L for 14D (Verschueren, 2001)
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Ethyl ether is a colorless, very volatile, mobile, hygroscopic liquid (below 34 degrees C (94 degrees F)) with a pungent, aromatic odor and a burning and sweet taste (AAR, 1998; (ACGIH, 1991; Ashford, 1994; Budavari, 1996; Harbison, 1998; ILO, 1998; Lewis, 1996; Lewis, 1997; Lewis, 1998; NFPA, 1997; Verschueren, 1983).
PH
VAPOR PRESSURE
- 442 mmHg (at 20 degrees C) (Lewis, 1996; Lewis, 1997; NFPA, 1997; Verschueren, 1983)
- 537.1 mmHg (at 25 degrees C) (Howard, 1993)
- 921 mmHg (at 40 degrees C) (Verschueren, 1983)
- 71.7 kPa (at 25 degrees C) (Lide, 1995)
184.9 mmHg (at 0 degrees C) (Budavari, 1996) 290.8 mmHg (at 10 degrees C) (Budavari, 1996) 439.8 mmHg (at 20 degrees C) (Budavari, 1996) 1276 mmHg (at 50 degrees C) (Budavari, 1996) 2304 mmHg (at 70 degrees C) (Budavari, 1996)
SPECIFIC GRAVITY
- STANDARD TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
LIQUID: 0.7249 (at 10/4 degrees C) (Budavari, 1996) LIQUID: 0.7134 (at 20/4 degrees C) (Budavari, 1996) LIQUID: 0.7135 (at 20/4 degrees C) (Lewis, 1996; Verschueren, 1983) LIQUID: 0.7019 (at 30/4 degrees C) (Budavari, 1996) LIQUID: 0.7146 (at 20/20 degrees C) (Clayton & Clayton, 1993) LIQUID: 0.7147 (at 20/20 degrees C) (Lewis, 1997)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
LIQUID: 0.72 kg/L (at 15 degrees C) (Ashford, 1994) LIQUID: 0.7138 gm/cm(3) (at 20 degrees C) (Lide, 1995)
FREEZING/MELTING POINT
-116 degrees C; -177 degrees F (Lide, 1995; NFPA, 1997) -116.2 degrees C (Lewis, 1996) -116.3 degrees C (stable crystals) (ACGIH, 1991; Budavari, 1996; Clayton & Clayton, 1993; ILO, 1998) -123.3 degrees C (metastable crystals) (Howard, 1993) 156.8 degrees K (Lide, 1995)
BOILING POINT
- -74.3 degrees C (at 1.0 mmHg) (Budavari, 1996)
- -48.1 degrees C (at 10 mmHg) (Budavari, 1996)
- -11.5 degrees C (at 100 mmHg) (Budavari, 1996)
- 2.2 degrees C (at 200 mmHg) (Budavari, 1996)
- 17.9 degrees C (at 400 mmHg) (Budavari, 1996)
- 34 degrees C (Ashford, 1994; Lide, 1995)
- 34.5 degrees C (ACGIH, 1991; Lewis, 1997)
- 34.6 degrees C (at 760 mmHg) (Budavari, 1996; Clayton & Clayton, 1993; Howard, 1993; ILO, 1998; Lewis, 1996)
- 35 degrees C; 94 degrees F (NFPA, 1994; (Verschueren, 1983)
- 307.6 degrees K (at 1 atm) (Lide, 1995)
FLASH POINT
- -40 degrees C (open cup) (Clayton & Clayton, 1993)
- -45 degrees C; -49 degrees F (Cleveland open cup/closed cup) (AAR, 1998; (ACGIH, 1991; Ashford, 1994; Budavari, 1996; ILO, 1998; Lewis, 1996; Lewis, 1997; Lide, 1995; NFPA, 1997)
AUTOIGNITION TEMPERATURE
- 160 degrees C; 320 degrees F (Lewis, 1996; NFPA, 1997)
- 180 degrees C; 356 degrees F (ACGIH, 1991; Lewis, 1997; Lide, 1995)
- 180-190 degrees C (Budavari, 1996)
EXPLOSIVE LIMITS
1.85% (ACGIH, 1991; Budavari, 1996; Lewis, 1996; Lewis, 1997) 1.9% (Clayton & Clayton, 1993; ILO, 1998; NFPA, 1997)
36% (ILO, 1998; Lewis, 1996; NFPA, 1997) 48% (ACGIH, 1991; Lewis, 1997)
SOLUBILITY
It is insoluble to slightly soluble in water; solubility in water is increased by hydrogen chloride (AAR, 1998; (Budavari, 1996; Clayton & Clayton, 1993; ILO, 1998; Lewis, 1996; Lewis, 1997; NFPA, 1997). 8.43 g/100 g (at 15 degrees C) (ACGIH, 1991; Ashford, 1994; Budavari, 1996; Verschueren, 1983) 69,000 mg/L (at 20 degrees C) (Verschueren, 1983) 6.05 g/100 g (at 25 degrees C) (hygroscopic) (ACGIH, 1991; Budavari, 1996) 54,950 mg/L (at 25 degrees C) (Howard, 1993) 60,500 mg/L (at 25 degrees C) (Verschueren, 1983)
Ethyl ether is very soluble in ethanol; it is soluble in sulfuric acid, acetone, and in concentrated hydrochloric acid. It is miscible with the lower aliphatic alcohols, benzene, chloroform, petroleum ether, solvent naphtha, other fat solvents, and many oils (ACGIH, 1991; Budavari, 1996; Clayton & Clayton, 1993; HSDB , 1999; Lewis, 1996; Lewis, 1997).
OCTANOL/WATER PARTITION COEFFICIENT
HENRY'S CONSTANT
- 8.69x10(-4) atm-m(3)/mol (Ehrenfeld et al, 1986)
- 0.00128 atm-m(3)/mol (at 25 degrees C) (Howard, 1993)
SPECTRAL CONSTANTS
OTHER/PHYSICAL
192.7 degrees C (Budavari, 1996) 466.74 degrees K (Lide, 1995)
1.35555 (at 15 degrees C) (Budavari, 1996) 1.3526 (at 20 degrees C) (Clayton & Clayton, 1993; Lewis, 1997)
0.283 cp (at 0 degrees C) (Lide, 1995) 0.00233 cp (at 20 degrees C) (Lewis, 1997) 0.2448 cp (at 20 degrees C) (Budavari, 1996) 0.224 cp (at 25 degrees C) (Lide, 1995)
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