VINYL TOLUENE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
VINYL TOLUENE BENZENE, ETHENYLMETHYL- ETHENYLMETHYLBENZENE METHYLETHENYLBENZENE METHYL STYRENE alpha, beta-STYRENE STYRENE, AR-METHYL- STYRENE, METHYL- TOLUENE, VINYL- (Mixed Isomers) TOLYLETHYLENE 3-VINYL TOLUENE (Mixed Isomers) 4-VINYL TOLUENE (Mixed Isomers) m-VINYL TOLUENE p-VINYL TOLUENE VINYL TOLUENE, INHIBITED (Mixed Isomers) VINYL TOLUENE, UNINHIBITED (Mixed Isomers) TOLUENE, VINYL- TOLUENE, VINYL- (MIXED ISOMER) VINYL TOLUENE, INHIBITED VINYL TOLUENE, INHIBITED (MIXED ISOMER) VINYL TOLUENE, MIXED ISOMER VINYL TOLUENE, UNINHIBITED VINYL TOLUENE, UNINHIBITED (MIXED ISOMER)
IDENTIFIERS
2618-Vinyltoluenes, inhibited 2618-Vinyltoluenes, stabilized
130-FLAMMABLE LIQUIDS (NON-POLAR / WATER-IMMISCIBLE / NOXIOUS)(for UN/NA Number2618) Polymerization Hazard (ERG, 2004)
SYNONYM REFERENCE
- (Hathaway, 1991;(HSDB , 1994)IATA, 1994; NIOSH, 1994;(RTECS, 1994)
USES/FORMS/SOURCES
Vinyl toluene's commercial use is primarily as a monomer in the plastics and surface-coating industries and as a component in the production of insecticides (ACGIH, 1991). It is used as a solvent and as a chemical intermediate (Lewis, 1993). Vinyl toluene is used in resin production and as a block-packaging component for radioactive waste (Clayton & Clayton, 1994).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Commercial vinyl toluene, also called METHYL STYRENE, is usually a mixture of the meta- and para- isomers in approximately a 60:40 ratio, but often the toxicological literature does not distinguish between the various possible forms. Ratios are identified here where deemed appropriate.
- Vinyl toluene is an irritant of the eyes and mucous membranes. At high concentrations, it causes narcosis in animals and it is expected that severe exposure will produce the same effect in humans.
- Vinyl toluene has been shown in laboratory experiments to be a teratogen. In experimental situations it has exhibited reproductive effects. Experiments have shown mutations.
- According to the 1983 National Occupational Exposure Survey, as many as 25,353 employees in 2,028 plants are potentially exposed to vinyl toluene in the US.
- The toxicologic properties of vinyl toluene appear to be similar to those of styrene. The following clinical effects information is for STYRENE, although NOT ALL OF THESE have been noted in patients with vinyl toluene exposure:
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
May cause toxic effects if inhaled or absorbed through skin. Inhalation or contact with material may irritate or burn skin and eyes. Fire will produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control or dilution water may cause pollution.
ACUTE CLINICAL EFFECTS
- The toxicity of vinyl toluene is similar to that of styrene. Vinyl toluene is an irritant of the eyes, nose, and mucous membranes at a concentration of approximately 400 ppm (Hathaway et al, 1991; ACGIH, 1991). The liquid is a skin irritant (Sittig, 1985; HSDB , 1996).
- Inhalation is the major exposure route (Snyder, 1987; Hathaway et al, 1991). The odor is detectable at 50 ppm, strong but tolerable at 200 ppm, and objectionable at 300 ppm (ACGIH, 1991). Vapor inhalation can cause drowsiness (Sittig, 1985). The anesthetic effects are similar to those of styrene (Clayton & Clayton, 1994).
- Although no cases have been reported, aspiration of ingested vinyl toluene into the lungs has the potential to cause serious or fatal chemical pneumonitis.
- Vinyl toluene is a moderate skin irritant in rabbits in the standard Draize test (RTECS , 1996; Hathaway et al, 1991). Vinyl toluene caused narcosis in mice, rats, rabbits, and guinea pigs exposed by the oral, inhalation, and dermal routes (HSDB , 1996; Hathaway et al, 1991). Mice exposed to vinyl toluene for 4 hours in an LD50 study developed pulmonary edema (RTECS , 1996).
- Vinyl toluene is apparently metabolized to corresponding styrene oxide intermediates by cytochrome P-450, and conjugated with glutathione to eventually form thioethers (Heinonen et al, 1982). Alternatively, the epoxides can be hydrolyzed to diols (Heinonen, 1984).
CHRONIC CLINICAL EFFECTS
- High-level occupational exposure to vinyl toluene has produced central nervous system depression, poor memory, slowed visual-motor performance, and electrophysiological changes (IARC, 1994).
- Defatting dermatitis can be caused by prolonged or repeated skin exposure (HSDB , 1996). Allergic contact dermatitis has also been reported (Sjoberg et al, 1982; Sjoberg et al, 1984). It was inactive in a guinea pig maximization test, however (Sjoberg et al, 1982).
- Hepatocellular necrosis was produced in mice with inhalation exposure to 200 ppm, 6 hours per day for 15 days (RTECS , 1996). Rats, guinea pigs, rabbits, and monkeys exposed to 1250 ppm in 92 to 100 7- to 8-hour exposures had increased kidney weights; NOAEL was 600 ppm (ACGIH, 1991; HSDB , 1996). Nephropathy was evident in male, but not female, rats exposed to 160 to 1000 ppm for 6 hours/day, 5 days/week for 13 weeks (ACGIH, 1991).
- Mice exposed to 160 ppm for 6 hours/day, 5 days/week for 13 weeks developed pulmonary inflammation (ACGIH, 1991). Non-neoplastic proliferation of the nasal mucosa occurred in rats exposed to 100 or 300 ppm, and in mice exposed to 10 or 25 ppm, for 2 years (ACGIH, 1991).
- Rats exposed to 100 to 300 ppm, 6 hours/day, 5 days/week for up to 15 weeks had reduced sensory and motor nerve conduction velocity, characteristic of axonal degeneration. The NOAEL was 50 ppm (Seppalainen & Savolainen, 1982a). Decreased amplitude of evoked motor nerve action potentials was also seen (Seppalainen & Savolainen, 1982b). No effects were seen with exposure for less than 12 weeks (Seppalainen & Savolainen, 1982).
- In a 2-year inhalation study conducted by the National Toxicology Program, there was no evidence of neurotoxicity in mice or rats exposed to vinyl toluene at concentrations up to 300 ppm (ACGIH, 1991).
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. Wash skin with soap and water. Keep victim warm and quiet. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
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. 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 - 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 - Do not induce emesis. DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting. 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. 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.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
The lowest published toxic concentration for a human (inhalation route) is 400 ppm (RTECS , 1995). Human subjects noted ocular and upper respiratory tract irritation at a 400 ppm vinyl toluene concentration; strong, objectionable odor at 300 ppm; and strong, tolerable odor at 200 ppm. At 50 ppm, the odor was detectable, but there was no irritation of mucous membranes. The odor was reported to be undetectable at less than 10 ppm (ACGIH, 1991). Another study concluded that the disagreeable odor became irritating at 50 ppm (ACGIH, 1991).
Exposure to 580 ppm is well tolerated by most laboratory animals (Clayton & Clayton, 1994). Exposure of guinea pigs to 1350 ppm for 7 hours/day for 100 days caused slight liver damage. There were no effects in female monkeys at this concentration (Hathaway et al, 1991). Rats tolerated exposure to 300 ppm for 60 hours without clinical symptoms, although they appeared relatively inactive (Hathaway et al, 1991). At this concentration, vinyl toluene was found to accumulate in perirenal fat and was more effective than styrene, xylene, or toluene in producing neurochemical effects as determined by enzyme assays.
The liquid dropped in the eyes of rabbits caused slight conjunctival irritation (Hathaway et al, 1991). Applied to rabbit skin, vinyl toluene produced erythema with the development of edema and superficial necrosis (Hathaway et al, 1991). In two-year toxicology and carcinogenesis studies, there was no evidence of carcinogenic activity for male or female rats exposed to 100 or 300 ppm by inhalation (6 hours/day, 5 days/week for 103 weeks), and no evidence of carcinogenic activity for male or female mice exposed to 10 or 25 ppm on the same schedule (Boorman G, 1990).
- Carcinogenicity Ratings for CAS25013-15-4 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: Vinyl toluene EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): 3 ; Listed as: Vinyl toluene 3 : The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.
NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Vinyl toluene 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 CAS25013-15-4 (U.S. Environmental Protection Agency, 2011):
CALCULATIONS
CONVERSION FACTORS 1 mg/m(3) = 0.206 ppm
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS25013-15-4 (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 CAS25013-15-4 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS25013-15-4 (National Institute for Occupational Safety and Health, 2007):
Listed as: Vinyl toluene REL: TWA: 100 ppm (480 mg/m(3)) STEL: Ceiling: Carcinogen Listing: (Not Listed) Not Listed Skin Designation: Not Listed Note(s):
IDLH: IDLH: 400 ppm Note(s): Not Listed
- OSHA PEL Values for CAS25013-15-4 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS25013-15-4 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS25013-15-4 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS25013-15-4 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS25013-15-4 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS25013-15-4 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS25013-15-4 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS25013-15-4 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS25013-15-4 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2618 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2618 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS25013-15-4 (NFPA, 2002):
Listed as: Vinyl Toluene Hazard Ratings: Health Rating (Blue): 2 Flammability Rating (Red): 2 Instability Rating (Yellow): 2 Oxidizer/Water-Reactive Designation: Not Listed
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Protect against physical damage (HSDB , 1994). Store in a cool, dry, well-ventilated location (HSDB , 1994). Outside or detached storage is preferred (HSDB , 1994).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
- Avoid breathing vapors. Keep upwind. Wear appropriate chemical protective gloves, boots and goggles. Do not handle broken packages unless wearing appropriate personal protective equipment. Wash away any material which may have contacted the body with copious amounts of water or soap and water (AAR, 1992).
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 25013-15-4.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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.
Vinyl toluene is flammable when exposed to heat or flame (Lewis, 1992).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS25013-15-4 (NFPA, 2002):
Listed as: Vinyl Toluene Flammability Rating: 2
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
Water spray, fog or regular foam. Do not use straight streams. Move containers from fire area if you can do it without risk.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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 CAS25013-15-4 (NFPA, 2002):
- Do not extinguish fire unless flow can be stopped. Use water in flooding quantities as fog. Solid streams of water may spread fire. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Use foam, dry chemical, or carbon dioxide to fight fire (AAR, 1992).
- If fire involving vinyl toluene becomes uncontrollable or container is exposed to direct flame, consider evacuation of one-third mile radius (AAR, 1992).
EXPLOSION HAZARD
- At elevated temperatures, vapors of vinyl toluene mixed with air may be explosive, and polymerization may occur under explosive expansion (ACGIH, 1991).
DUST/VAPOR HAZARD
- At elevated temperatures, vapors of vinyl toluene mixed with air may be explosive, and polymerization may occur under explosive expansion (ACGIH, 1991).
REACTIVITY HAZARD
- CAUTION: This material may polymerize violently under high temperature conditions or upon contamination with other products. Polymerization will produce heat and high pressure buildup in containers which may lead to an explosion or container rupture (ERG, 2004).
- Vinyl toluene is flammable when exposed to heat or flame. It can react vigorously with oxidizing materials (Lewis, 1992).
- If vinyl toluene is subject to heat for prolonged periods or becomes contaminated, it is subject to polymerization with release of heat. If the polymerization takes place inside a container, the container is subject to violent rupture (AAR, 1992).
- Vinyl toluene is incompatible with oxidizing agents, and with catalysts for vinyl polymerization, such as peroxides, strong acids, and aluminum chloride (HSDB , 1994).
- When heated to decomposition, vinyl toluene emits acrid smoke and irritating fumes (Lewis, 1992).
- At elevated temperatures, vapors of vinyl toluene mixed with air may be explosive, and polymerization may occur under explosive expansion (ACGIH, 1991).
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 130 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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 130 (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 fire involving vinyl toluene becomes uncontrollable or container is exposed to direct flame, consider evacuation of one-third mile radius (AAR, 1992).
- AIHA ERPG Values for CAS25013-15-4 (AIHA, 2006):
- DOE TEEL Values for CAS25013-15-4 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS25013-15-4 (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; 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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 CAS25013-15-4 (National Institute for Occupational Safety and Health, 2007):
IDLH: 400 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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 130 (ERG, 2004) At the time of this review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices (HSDB , 1994). Incineration is a possible method of disposal for vinyl toluene (HSDB , 1994).
LARGE SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004) Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. Build dikes to contain flow as necessary. Use water spray to knock down vapors (AAR, 1992). Vinyl toluene will float in slick on surface and dissolve slowly (OHM/TADS , 1994).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Vinyl toluene may be released to the environment in wastewater and emissions resulting from its manufacture and its use in resin production and the plastics industry. Vinyl toluene may also be released in engine exhaust, wood smoke, emissions from the combustion of polyethylene and polystyrene polymers, and volatile emissions from polychloroprene-based building materials (HSDB , 1994).
- Vinyl toluene may form in the environment as a biodegradation product of ethyltoluene (HSDB , 1994).
- o-Vinyl toluene has been identified in the essential oil of a Mississippi salt marsh plant (HSDB , 1994).
ENVIRONMENTAL FATE AND KINETICS
The relatively high vapor pressure of the commercial mixture of vinyl toluene, 1.1 mmHg at 20 degrees C, suggests that the o-, m- and p- isomers would exist almost entirely in the vapor phase in the atmosphere. If released to the atmosphere, vinyl toluene may react with photochemically generated hydroxyl radicals and ozone molecules (estimated overall half-life 6 hours) or it may photolyze (HSDB , 1994).
SURFACE WATER If released to water, vinyl toluene could potentially volatilize (estimated half-life 10 days from a model pond), photolyze, react with naturally occurring oxidants found in the water (half-life approximately 8 days), or adsorb to suspended solids and sediments in water (HSDB , 1994).
TERRESTRIAL If released to soil, vinyl toluene is predicted to be moderately mobile. This compound has the potential to undergo photolysis on surface soils. Volatilization may be a significant removal process (HSDB , 1994).
OTHER AIR: The estimated overall half-life of vinyl toluene in the atmosphere via reaction with photochemically generated hydroxyl radicals and ozone molecules is 6 hours (HSDB , 1994). WATER: The estimated half-life of vinyl toluene in water via volatilization is 10 days from a model pond. The half-life from reaction with naturally occurring oxidants found in the water is approximately 8 days (HSDB , 1994).
BIODEGRADATION
- Bioaccumulation in aquatic organisms is not expected to be an important fate process (HSDB , 1994).
ENVIRONMENTAL TOXICITY
- No information found at the time of this review.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Vinyl toluene is a colorless liquid with what has been described as an aromatic, strong, or disagreeable odor (AAR, 1992; ACGIH, 1991; Lewis, 1993).
- No information on the taste of vinyl toluene was found at the time of this review.
- It occurs commercially as a mixture primarily of the meta- (50% to 70%) and para- (30% to 45%) isomers (ACGIH, 1991).
- Vinyl toluene is produced by the dehydrogenation of meta- and para-ethyl toluene or by catalytic reforming (ACGIH, 1991).
PH
VAPOR PRESSURE
- 1.1 mmHg (at 20 degrees C) (ACGIH, 1991)
- 1.1 mmHg; 0.146 kPa (at 20 degrees C) (Snyder, 1987)
SPECIFIC GRAVITY
- NORMAL TEMPERATURE AND PRESSURE
(25 degrees C; 77 degrees F and 760 mmHg) LIQUID MONOMER: 0.890 (at 25/25 degrees C) (Lewis, 1993) POLYMER: 1.027 (at 25/25 degrees C) (Snyder, 1987)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
-77 degrees C (ACGIH, 1991) -76.8 degrees C (Lewis, 1993; Snyder, 1987)
BOILING POINT
- 168 degrees C (Sittig, 1985)
- 170-171 degrees C (Lewis, 1993)
- 172 degrees C (ACGIH, 1991)
- The boiling point of any given sample of vinyl toluene would depend upon the relative amounts of different isomers present.
FLASH POINT
- 60 degrees C (open cup) (ACGIH, 1991)
- 54.4 degrees C; 130 degrees F (closed cup) (Snyder, 1987; Lewis, 1993)
AUTOIGNITION TEMPERATURE
- 494 degrees C; 921 degrees F (Lewis, 1993)
- 538 degrees C; 1000 degrees F (NFPA, 1991)
EXPLOSIVE LIMITS
1.9% (ACGIH, 1991) 0.8% (NFPA, 1991)
6.1% (ACGIH, 1991) 11.0% (NFPA, 1991)
SOLUBILITY
Vinyl toluene is very slightly soluble in water (Lewis, 1993). Solubility in Water: 0.0089 g/100 g (at 25 degrees C) (ACGIH, 1991)
Vinyl toluene is soluble in methanol and ether (Lewis, 1993). It is very soluble in acetone, ethanol, carbon tetrachloride, and benzene (ACGIH, 1991). It is also soluble in diethyl ether, n-heptane, and ethanol (HSDB , 1994).
OTHER/PHYSICAL
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