| Section 1. Identification | |||
|---|---|---|---|
| Chemical Name | isopropenyl acetate | CAS No. | 108-22-5 |
| Synonyms | acetatic acid,isopro-penyl ester | Chinese Name | 乙酸异丙烯酯 |
| Molecular Formula | C_5H_8O_2 | Molecular Weight | 100.1158 |
| UN No. | 2403 | Data Source | PubChem (NIH/NLM) |
| GHS Hazard Classification | |
|---|---|
| Signal Word | DANGER |
| Pictograms | GHS02 · Flammable GHS07 · Irritant |
| Hazard Statements | H225H335 |
| Precautionary Statements | P210P233P240P241P242P243P261P271P280P303+P361+P353P304+P340P319P370+P378P403+P233P403+P235P405P501 |
| Contents | |||
|---|---|---|---|
| Section 2 | Hazards Identification | Section 4 | First-Aid Measures |
| Section 5 | Fire-Fighting Measures | Section 6 | Accidental Release Measures |
| Section 7 | Handling and Storage | Section 8 | Exposure Controls / Personal Protection |
| Section 9 | Physical and Chemical Properties | Section 10 | Stability and Reactivity |
| Section 11 | Toxicological Information | Section 12 | Ecological Information |
| Section 13 | Disposal Considerations | Section 14 | Transport Information |
H225 (100%): Highly Flammable liquid and vapor [Danger Flammable liquids]
H335 (45.7%): May cause respiratory irritation [Warning Specific target organ toxicity, single exposure; Respiratory tract irritation]
P210, P233, P240, P241, P242, P243, P261, P271, P280, P303+P361+P353, P304+P340, P319, P370+P378, P403+P233, P403+P235, P405, and P501 (click each P-code to see the statement)
Aggregated GHS information provided per 300 reports by companies from 8 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies.
Information may vary between notifications depending on impurities, additives, and other factors. The percentage value in parenthesis indicates the notified classification ratio from companies that provide hazard codes. Only hazard codes with percentage values above 10% are shown. For more detailed information, please visit ECHA C&L website.
Excerpt from ERG Guide 129 [Flammable Liquids (Water-Miscible / Noxious); polymerization hazard]:
Refer to the "General First Aid" section. Specific First Aid: 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. (ERG, 2024)
General First Aid:
· Call 911 or emergency medical service.
· Ensure that medical personnel are aware of the material(s) involved, take precautions to protect themselves and avoid contamination.
· Move victim to fresh air if it can be done safely.
· Administer oxygen if breathing is difficult.
· If victim is not breathing:
-- DO NOT perform mouth-to-mouth resuscitation; the victim may have ingested or inhaled the substance.
-- If equipped and pulse detected, wash face and mouth, then give artificial respiration using a proper respiratory medical device (bag-valve mask, pocket mask equipped with a one-way valve or other device).
-- If no pulse detected or no respiratory medical device available, provide continuous compressions. Conduct a pulse check every two minutes or monitor for any signs of spontaneous respirations.
· Remove and isolate contaminated clothing and shoes.
· For minor skin contact, avoid spreading material on unaffected skin.
· In case of contact with substance, remove immediately by flushing skin or eyes with running water for at least 20 minutes.
· For severe burns, immediate medical attention is required.
· Effects of exposure (inhalation, ingestion, or skin contact) to substance may be delayed.
· Keep victim calm and warm.
· Keep victim under observation.
· For further assistance, contact your local Poison Control Center.
· Note: Basic Life Support (BLS) and Advanced Life Support (ALS) should be done by trained professionals.
Specific First Aid:
· 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.
In Canada, an Emergency Response Assistance Plan (ERAP) may be required for this product. Please consult the shipping paper and/or the "ERAP" section.
Excerpt from ERG Guide 129 [Flammable Liquids (Water-Miscible / Noxious); polymerization hazard]:
CAUTION: The majority of these products have a very low flash point. Use of water spray when fighting fire may be inefficient.
SMALL FIRE: Dry chemical, CO2, water spray or alcohol-resistant foam. Do not use dry chemical extinguishers to control fires involving nitromethane (UN1261) or nitroethane (UN2842).
LARGE FIRE: Water spray, fog or alcohol-resistant foam. Avoid aiming straight or solid streams directly onto the product. If it can be done safely, move undamaged containers away from the area around the fire.
FIRE INVOLVING TANKS, RAIL TANK CARS OR HIGHWAY TANKS: Fight fire from maximum distance or use unmanned master stream devices 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 in direct contact with flames. For massive fire, use unmanned master stream devices or monitor nozzles; if this is impossible, withdraw from area and let fire burn. (ERG, 2024)
Alcohol foam. Water may be ineffective.
· CALL 911. Then call emergency response telephone number on shipping paper. If shipping paper not available or no answer, refer to appropriate telephone number listed on the inside back cover.
· Keep unauthorized personnel away.
· Stay upwind, uphill and/or upstream.
· Ventilate closed spaces before entering, but only if properly trained and equipped.
· ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from 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.
Large Spill
· Dike far ahead of liquid spill for later disposal.
· Water spray may reduce vapor, but may not prevent ignition in closed spaces.
Excerpt from ERG Guide 129 [Flammable Liquids (Water-Miscible / Noxious); polymerization hazard]:
IMMEDIATE PRECAUTIONARY MEASURE: Isolate spill or leak area for at least 50 meters (150 feet) in all directions.
LARGE SPILL: Consider initial downwind evacuation for at least 300 meters (1000 feet).
FIRE: If tank, rail tank car or highway tank 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. (ERG, 2024)
Immediate precautionary measure
· Isolate spill or leak area for at least 50 meters (150 feet) in all directions.
· Consider initial downwind evacuation for at least 300 meters (1000 feet).
· If tank, rail tank car or highway tank 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.
SRP: At the time of review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices.
Excerpt from ERG Guide 129 [Flammable Liquids (Water-Miscible / Noxious); polymerization hazard]:
ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from 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.
LARGE SPILL: Dike far ahead of liquid spill for later disposal. Water spray may reduce vapor, but may not prevent ignition in closed spaces. (ERG, 2024)
· Wear positive pressure self-contained breathing apparatus (SCBA).
· Structural firefighters' protective clothing provides thermal protection but only limited chemical protection.
10.0 [ppm]
CAUTION: The majority of these products have a very low flash point. Use of water spray when fighting fire may be inefficient.
Small Fire
· Dry chemical, CO2, water spray or alcohol-resistant foam.
· Do not use dry chemical extinguishers to control fires involving nitromethane (UN1261) or nitroethane (UN2842).
Large Fire
· Water spray, fog or alcohol-resistant foam.
· Avoid aiming straight or solid streams directly onto the product.
· If it can be done safely, move undamaged containers away from the area around the fire.
Fire Involving Tanks, Rail Tank Cars or Highway Tanks
· Fight fire from maximum distance or use unmanned master stream devices 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 in direct contact with flames.
· For massive fire, use unmanned master stream devices or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
Excerpt from ERG Guide 129 [Flammable Liquids (Water-Miscible / Noxious); polymerization hazard]:
Wear positive pressure self-contained breathing apparatus (SCBA). Structural firefighters' protective clothing provides thermal protection but only limited chemical protection. (ERG, 2024)
Isopropenyl acetate appears as a clear colorless liquid. Less dense than water. Vapors heavier than air. Used to make other chemicals.
White liquid; [Hawley] Colorless liquid; [MSDSonline]
WATER WHITE LIQUID
-92.9 °C
60 °F (NFPA, 2010)
60 °F (16 °C) (CLOSED CUP)
Soluble in ethanol and acetone, very soluble in ethyl ether.
Solubility in water 3.25% by weight.
0.9090 g/cu cm at 20 °C
45.2 [mmHg]
45 mm Hg at 25 °C
808 °F (431 °C)
When heated to decomposition it emits acrid smoke and irritating fumes.
INDEX OF REFRACTION: 1.4001 AT 20 °C/D
CONVERSION FACTORS: 1 MG/L= 245 PPM; 1 PPM= 4.1 MG/CU M
Boiling point
Heat of sublimation
Optical coefficient
Refractive index
Thermal expansion coefficient
Vapor pressure
Viscosity
Other Classes -> Esters, Other
Flammable agents - 3rd degree
Reactive agents - 1st degree
EU Flavoring substances
FLAVORING AGENT OR ADJUVANT -> FDA Substance added to food
Highly flammable. Soluble in water.
Esters, Sulfate Esters, Phosphate Esters, Thiophosphate Esters, and Borate Esters
Hydrocarbons, Aliphatic Unsaturated
Polymerizable Compounds
Highly Flammable
Polymerizable
ISOPROPENYL ACETATE is an ester. Esters react with acids to liberate heat along with alcohols and acids. Strong oxidizing acids may cause a vigorous reaction that is sufficiently exothermic to ignite the reaction products. Heat is also generated by the interaction of esters with caustic solutions. Flammable hydrogen is generated by mixing esters with alkali metals and hydrides.
Neurotoxin - Acute solvent syndrome
MILD IRRITANT. .../CNS DEPRESSANT/ IN HIGH CONCENTRATIONS.
THREE OF SIX RATS DIED FOLLOWING INHALATION OF 4,000 PPM FOR 4 HR. IT CAUSED SLIGHT SKIN IRRITATION IN RABBITS. /FROM TABLE/
Isopropenyl acetate's use as a reagent for acylation of enols may result in its release to the environment through various waste streams. If released to air, a vapor pressure of 45 mm Hg at 25 °C indicates isopropenyl acetate is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase isopropenyl acetate will be degraded in the atmosphere by reaction with ozone and photochemically-produced hydroxyl radicals; estimated half-lives for these reactions are 24 and 7.5 hours, respectively. If released to soil, isopropenyl acetate is expected to have high mobility based upon an estimated Koc of 120. Volatilization from wet soil surfaces is expected to occur based on an estimated Henry's Law constant of 1.8X10-3 atm-cu m/mole. This compound's vapor pressure indicates that volatilization from dry soil surfaces may potentially occur. If released into water, adsorption to suspended solids and sediment in the water column is not expected given the estimated Koc for this compound. Volatilization from water surfaces is expected based upon this compound's Henry's Law constant. Estimated volatilization half-lives for a model river and model lake are 3.4 hours and 4.1 days, respectively. The potential for bioconcentration in aquatic organisms is low based upon the estimated BCF of 5.5. Hydrolysis is not expected to be an important process based upon estimated half-lives of 300 and 30 days at pHs 7 and 8, respectively. Occupational exposure to isopropenyl acetate may occur through inhalation and dermal contact with this compound at workplaces where isopropenyl acetate is produced or used. (SRC)
Isopropenyl acetate's use as a reagent for acylation of enols(1) may result in its release to the environment through various waste streams(SRC).
TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 120(SRC), determined from an estimated log Kow of 1.3(2,SRC) and a regression-derived equation(3), indicates that isopropenyl acetate is expected to have high mobility in soil(SRC). Volatilization of isopropenyl acetate from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 1.8X10-3 atm-cu m/mole(SRC), using a fragment constant estimation method(4). The potential for volatilization of isopropenyl acetate from dry soil surfaces may exist(SRC) based on a vapor pressure of 45 mm Hg(5).
AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 120(SRC), determined from an estimated log Kow of 1.3(2,SRC) and a regression-derived equation(3), indicates that isopropenyl acetate is not expected to adsorb to suspended solids and sediment in water(SRC). Isopropenyl acetate is expected to volatilize from water surfaces(3,SRC) based on an estimated Henry's Law constant of 1.8X10-3 atm-cu m/mole(SRC), developed using a fragment constant estimation method(4). Estimated volatilization half-lives for a model river and model lake are 3.4 hours and 4.1 days, respectively(3,SRC). According to a classification scheme(5), an estimated BCF of 5.5(3,SRC), from an estimated log Kow(2,SRC), suggests that bioconcentration in aquatic organisms is low(SRC). Estimated hydrolysis half-lives of 300 and 30 days at pHs 7 and 8, respectively(6), indicate that hydrolysis is not expected to be an important process(SRC).
ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), isopropenyl acetate, which has a vapor pressure of 45 mm Hg at 25 °C(2,SRC), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase isopropenyl acetate is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals and ozone(SRC); the half-lives for these reactions in air are estimated to be about 7.5 and 24 hours, respectively(3,SRC).
The rate constant for the vapor-phase reaction of isopropenyl acetate with photochemically-produced hydroxyl radicals has been estimated as 5.2X10-11 cu cm/molecule-sec at 25 °C(SRC) using a structure estimation method(1,SRC). This corresponds to an atmospheric half-life of about 7.5 hours at an atmospheric concentration of 5X10+5 hydroxyl radicals per cu cm(1,SRC). The rate constant for the vapor-phase reaction of isopropenyl acetate with ozone has been estimated as 1.1X10-17 cu cm/molecule-sec at 25 °C(1,SRC). This corresponds to an atmospheric half-life of about 24 hours at an atmospheric ozone concn of 7X10+11 cu cm/molecule-sec at 25 °C(1,SRC). A base-catalyzed second-order hydrolysis rate constant of 0.27 L/mol-sec(SRC) was estimated using a structure estimation method(2); this corresponds to half-lives of 300 and 30 days at pH values of 7 and 8, respectively(2,SRC).
An estimated BCF of 5.5 was calculated for isopropenyl acetate(SRC), using an estimated log Kow of 1.3(1,SRC) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests that bioconcentration in aquatic organisms is low(SRC).
The Koc of isopropenyl acetate is estimated as approximately 120(SRC), using an estimated log Kow of 1.3(1) and a regression-derived equation(2,SRC). According to a classification scheme(3), this estimated Koc value suggests that isopropenyl acetate is expected to have high mobility in soil(SRC).
The Henry's Law constant for isopropenyl acetate is estimated as 1.8X10-3 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that isopropenyl acetate is expected to volatilize rapidly from water surfaces(2,SRC). Based on this Henry's Law constant, the estimated volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec) is estimated as approximately 3.4 hours(2,SRC). The estimated volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec) is estimated as approximately 4.1 days(2,SRC). Isopropenyl acetate's Henry's Law constant(1,SRC) indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of isopropenyl acetate from dry soil surfaces may exist(SRC) based on a vapor pressure of 45 mm Hg(3).
Occupational exposure to isopropenyl acetate may occur through inhalation and dermal contact with this compound at workplaces where isopropenyl acetate is produced or used. (SRC)
Isopropenyl acetate's use as a reagent for acylation of enols may result in its release to the environment through various waste streams. If released to air, a vapor pressure of 45 mm Hg at 25 °C indicates isopropenyl acetate is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase isopropenyl acetate will be degraded in the atmosphere by reaction with ozone and photochemically-produced hydroxyl radicals; estimated half-lives for these reactions are 24 and 7.5 hours, respectively. If released to soil, isopropenyl acetate is expected to have high mobility based upon an estimated Koc of 120. Volatilization from wet soil surfaces is expected to occur based on an estimated Henry's Law constant of 1.8X10-3 atm-cu m/mole. This compound's vapor pressure indicates that volatilization from dry soil surfaces may potentially occur. If released into water, adsorption to suspended solids and sediment in the water column is not expected given the estimated Koc for this compound. Volatilization from water surfaces is expected based upon this compound's Henry's Law constant. Estimated volatilization half-lives for a model river and model lake are 3.4 hours and 4.1 days, respectively. The potential for bioconcentration in aquatic organisms is low based upon the estimated BCF of 5.5. Hydrolysis is not expected to be an important process based upon estimated half-lives of 300 and 30 days at pHs 7 and 8, respectively. Occupational exposure to isopropenyl acetate may occur through inhalation and dermal contact with this compound at workplaces where isopropenyl acetate is produced or used. (SRC)
Isopropenyl acetate's use as a reagent for acylation of enols(1) may result in its release to the environment through various waste streams(SRC).
TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 120(SRC), determined from an estimated log Kow of 1.3(2,SRC) and a regression-derived equation(3), indicates that isopropenyl acetate is expected to have high mobility in soil(SRC). Volatilization of isopropenyl acetate from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 1.8X10-3 atm-cu m/mole(SRC), using a fragment constant estimation method(4). The potential for volatilization of isopropenyl acetate from dry soil surfaces may exist(SRC) based on a vapor pressure of 45 mm Hg(5).
AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 120(SRC), determined from an estimated log Kow of 1.3(2,SRC) and a regression-derived equation(3), indicates that isopropenyl acetate is not expected to adsorb to suspended solids and sediment in water(SRC). Isopropenyl acetate is expected to volatilize from water surfaces(3,SRC) based on an estimated Henry's Law constant of 1.8X10-3 atm-cu m/mole(SRC), developed using a fragment constant estimation method(4). Estimated volatilization half-lives for a model river and model lake are 3.4 hours and 4.1 days, respectively(3,SRC). According to a classification scheme(5), an estimated BCF of 5.5(3,SRC), from an estimated log Kow(2,SRC), suggests that bioconcentration in aquatic organisms is low(SRC). Estimated hydrolysis half-lives of 300 and 30 days at pHs 7 and 8, respectively(6), indicate that hydrolysis is not expected to be an important process(SRC).
ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), isopropenyl acetate, which has a vapor pressure of 45 mm Hg at 25 °C(2,SRC), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase isopropenyl acetate is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals and ozone(SRC); the half-lives for these reactions in air are estimated to be about 7.5 and 24 hours, respectively(3,SRC).
The rate constant for the vapor-phase reaction of isopropenyl acetate with photochemically-produced hydroxyl radicals has been estimated as 5.2X10-11 cu cm/molecule-sec at 25 °C(SRC) using a structure estimation method(1,SRC). This corresponds to an atmospheric half-life of about 7.5 hours at an atmospheric concentration of 5X10+5 hydroxyl radicals per cu cm(1,SRC). The rate constant for the vapor-phase reaction of isopropenyl acetate with ozone has been estimated as 1.1X10-17 cu cm/molecule-sec at 25 °C(1,SRC). This corresponds to an atmospheric half-life of about 24 hours at an atmospheric ozone concn of 7X10+11 cu cm/molecule-sec at 25 °C(1,SRC). A base-catalyzed second-order hydrolysis rate constant of 0.27 L/mol-sec(SRC) was estimated using a structure estimation method(2); this corresponds to half-lives of 300 and 30 days at pH values of 7 and 8, respectively(2,SRC).
An estimated BCF of 5.5 was calculated for isopropenyl acetate(SRC), using an estimated log Kow of 1.3(1,SRC) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests that bioconcentration in aquatic organisms is low(SRC).
The Koc of isopropenyl acetate is estimated as approximately 120(SRC), using an estimated log Kow of 1.3(1) and a regression-derived equation(2,SRC). According to a classification scheme(3), this estimated Koc value suggests that isopropenyl acetate is expected to have high mobility in soil(SRC).
The Henry's Law constant for isopropenyl acetate is estimated as 1.8X10-3 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that isopropenyl acetate is expected to volatilize rapidly from water surfaces(2,SRC). Based on this Henry's Law constant, the estimated volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec) is estimated as approximately 3.4 hours(2,SRC). The estimated volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec) is estimated as approximately 4.1 days(2,SRC). Isopropenyl acetate's Henry's Law constant(1,SRC) indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of isopropenyl acetate from dry soil surfaces may exist(SRC) based on a vapor pressure of 45 mm Hg(3).
Occupational exposure to isopropenyl acetate may occur through inhalation and dermal contact with this compound at workplaces where isopropenyl acetate is produced or used. (SRC)
SRP: At the time of review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices.
/GUIDE 129P: FLAMMABLE LIQUIDS (POLAR/WATER-MISCIBLE/NOXIOUS)/ Fire or Explosion: 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 confined areas (sewers, basements, tanks). Vapor explosion hazard indoors, outdoors or in sewers. Those substances designated with "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.
/GUIDE 129P: FLAMMABLE LIQUIDS (POLAR/WATER-MISCIBLE/NOXIOUS)/ Health: 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.
/GUIDE 129P: FLAMMABLE LIQUIDS (POLAR/WATER-MISCIBLE/NOXIOUS)/ Public Safety: CALL Emergency Response Telephone Number ... . 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.
/GUIDE 129P: FLAMMABLE LIQUIDS (POLAR/WATER-MISCIBLE/NOXIOUS)/ Protective Clothing: Wear positive pressure self-contained breathing apparatus (SCBA). Structural firefighters' protective clothing will only provide limited protection.
For more DOT Emergency Guidelines (Complete) data for 1-PROPEN-2-OL, ACETATE (8 total), please visit the HSDB record page.
2403 129P
Flammable Liquid