ANISOLE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
Anisole Anizol Benzene, methoxy- Ether, methyl phenyl Methoxybenzene Methyl phenyl ether Metil fenil eter (Spanish) Phenyl methyl ether ANISOLE (AROMATIC ETHER) METHOXYBENZENE (AROMATIC ETHER) PHENYL METHYL ETHER (AROMATIC ETHER)
IDENTIFIERS
SYNONYM REFERENCE
- (DTP NCI/NIH, 2004; HSDB, 2003; RTECS, 2003; Pohanish, 2002; Lide, 1996)
USES/FORMS/SOURCES
Anisole is an important intermediate in the manufacture of organic compounds, including pharmaceuticals, fragrances, and food flavoring, particularly for meats (HSDB, 2003). Anisole has been used in the manufacture of soaps, detergents, creams, lotions, and perfumes since the 1930s. It is also used as a solvent, vermicide, chemical intermediate, and heat transfer medium (HSDB, 2003; Budavari, 2001; Lewis, 1997; Opdyke, 1979).
Anisole exists as a clear, colorless or straw-colored liquid. It possesses an aromatic odor, redolent of anise (AAR, 2002; Lewis, 2000).
Anisole is found in Artemisia dracunculus var turkestanica (tarragon), and has also been isolated from essential oil of Ocimum selloi (basil) (HSDB, 2003; Furia & Bellanca, 1975). Anisole is formed naturally and anthropogenically through hydrocarbon combustion. It may be emitted in automobile exhaust and in fumes from kerosene space heaters. Anisole may also occur naturally in meat or be formed during cooking (HSDB, 2003) . Anisole is derived through the following chemical reactions : phenol plus dimethyl sulfate (methylation) (Ashford, 2001) phenol plus methanol (catalytic gas-phase methylation) (Ashford, 2001) sodium phenate plus methyl chloride (Lewis, 2001a) phenol plus methyl chloride in presence of sodium hydroxide (Budavari, 2001) from bromobenzene by passing methyl chloride into a suspension of sodium phenolate in liquid ammonia (Budavari, 2001)
Anisole may occur as an impurity in the production of o-cresol and 2,6-xylenol through alkylation of phenol with methanol (HSDB, 2003) .
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Human volunteers exposed to anisole have experienced eye irritation, burning in the throat, and a foreign taste in the mouth. Other signs and symptoms of exposure may include cough; wheezing; sore throat; skin irritation; dry red skin; pain and redness of the eyes; dizziness; and lightheadedness. Prolonged exposure may cause drying and cracking of the skin.
- In experimental animals, anisole was an irritant and CNS depressant. Seizures or an effect on the seizure threshold, tremor, excitement, hematuria, and changes in the function or structure of salivary glands have also been observed.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (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 or dilution water may cause pollution.
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
- Esophageal or gastrointestinal tract irritation or burns may occur following an ingestion. The role of gastric decontamination is unclear.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (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.
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 Esophageal or gastrointestinal tract irritation or burns may occur following an ingestion. The role of gastric decontamination is unclear. PREHOSPITAL ACTIVATED CHARCOAL ADMINISTRATION Consider prehospital administration of activated charcoal as an aqueous slurry in patients with a potentially toxic ingestion who are awake and able to protect their airway. Activated charcoal is most effective when administered within one hour of ingestion. Administration in the prehospital setting has the potential to significantly decrease the time from toxin ingestion to activated charcoal administration, although it has not been shown to affect outcome (Alaspaa et al, 2005; Thakore & Murphy, 2002; Spiller & Rogers, 2002). In patients who are at risk for the abrupt onset of seizures or mental status depression, activated charcoal should not be administered in the prehospital setting, due to the risk of aspiration in the event of spontaneous emesis. The addition of flavoring agents (cola drinks, chocolate milk, cherry syrup) to activated charcoal improves the palatability for children and may facilitate successful administration (Guenther Skokan et al, 2001; Dagnone et al, 2002).
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
Oral doses of 1230 mg/kg four times daily resulted in death in 1 of 6 rats. No macroscopic liver damage was seen (Taylor et al, 1964). A minimum lethal (LDLo) intraperitoneal dose to rats of 500 mg/kg is reported (RTECS, 2004).
MAXIMUM TOLERATED EXPOSURE
Mice who had a 10% solution applied to one third of the body surface did not experience toxic effects (Lebedev, 1969). A calf who had a whole body application of a 10% solution did not experience toxic effects (Lebedev, 1969).
- Carcinogenicity Ratings for CAS100-66-3 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed 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 CAS100-66-3 (U.S. Environmental Protection Agency, 2011):
LC50- (INHALATION)MOUSE: LC50- (INHALATION)RAT: LD- (INTRAPERITONEAL)RAT: LD50- (ORAL)MOUSE: LD50- (SKIN)RABBIT: LD50- (INTRAPERITONEAL)RAT: LD50- (ORAL)RAT: LD50- (SUBCUTANEOUS)RAT: LDLo- (INTRAPERITONEAL)RAT: TCLo- (INHALATION)RAT: TDLo- (ORAL)RAT: TDLo- (ORAL)RAT: TDLo- (ORAL)RAT:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS100-66-3 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS100-66-3 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS100-66-3 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS100-66-3 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS100-66-3 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS100-66-3 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS100-66-3 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS100-66-3 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS100-66-3 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS100-66-3 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS100-66-3 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS100-66-3 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2222 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2222 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS100-66-3 (NFPA, 2002):
Listed as: Anisole Hazard Ratings: Health Rating (Blue): 1 Flammability Rating (Red): 2 Instability Rating (Yellow): 0 Oxidizer/Water-Reactive Designation: Not Listed
-HANDLING AND STORAGE
SUMMARY
Workers involved with anisole should be properly trained on its safe handling and storage (Pohanish, 2002). Contact with anisole should be avoided through the use of appropriate chemical protective clothing, such as solvent-resistant gloves, suits, boots, and goggles (AAR, 2002; Pohanish, 2002). Due to its flammability, ignition sources (sparks, flames, smoking) should be eliminated in the immediate area where anisole is used, handled or stored (AAR, 2002; Pohanish, 2002). A confined space where anisole is present should be monitored for exploisive levels prior to entry (Pohanish, 2002).
- PUBLIC HEALTH CONSIDERATIONS
Contaminated clothing and shoes should be removed and isolated (AAR, 2002). Contact with anisole should be avoided through the use of appropriate chemical protective clothing, such as solvent-resistant gloves, suits, boots, or goggles (AAR, 2002; Pohanish, 2002). Emergency showers and eyewash stations should be located nearby (Pohanish, 2002).
HANDLING
- Appropriate training on the safe handling and storage of anisole should be performed prior to an employee working with the material (Pohanish, 2002).
- Proper PPE should be worn when handling anisole. Broken containers or packages should not be handled unless appropriate PPE is worn (AAR, 2002; Pohanish, 2002).
- Anisole is highly flammable and may form explosive mixtures with air. Sparks, flames, and other potential ignition sources should be eliminated from immediate areas where it is used, handled, or stored. Non-sparking tools and equipment should be used when opening or closing anisole containers. Heated containers are also potentially explosive (AAR, 2002; (NIOSH ICSC, 2001); Pohanish, 2002).
- Anisole may form explosive vapor/air mixtures at temperatures above 52 degrees C. Explosion-proof electrical equipment, a closed system, and ventilation should be used where the potential for these higher temperature conditions exists ((NIOSH ICSC, 2001)).
STORAGE
Anisole should be stored in tightly closed containers. Non-sparking tools and equipment should be used when opening and closing containers (Pohanish, 2002). Metal containers for transferring anisole should be grounded and bonded. Drums should have self-closing valves, pressure vacuum bungs, and flame arresters (Pohanish, 2002).
- ROOM/CABINET RECOMMENDATIONS
Anisole should be stored in a cool, dry, ventilated, and fireproof location ((NIOSH ICSC, 2001); Pohanish, 2002).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
- Anisole is an eye, nose, throat, and skin irritant. Anisole can be moderately toxic when ingested or inhaled. Appropriate clean protective clothing (solvent-resistant gloves, suits, boots, goggles) and respiratory protection should be worn to avoid inhalation or bodily contact. Thorough, immediate washing with water or soap and water should be performed should eye or bodily contact occur (AAR, 2002; Lewis, 2000; Pohanish, 2002).
- Firefighting will necessitate use of positive pressure self-contained breathing apparatus (SCBA). An SCBA may also be used when an exposure limit is not established for any detectable concentration (AAR, 2002; Pohanish, 2002).
EYE/FACE PROTECTION
- Proper eye protection should be used when handling or working around anisole (AAR, 2002).
- Contact lenses should not be worn when working with anisole. Splash-proof chemical goggles or a protective face shield are recommended when a full-face respirator is not used (Pohanish, 2002).
RESPIRATORY PROTECTION
- Avoid breathing anisole vapors and keep upwind if possible. Avoid inhalation exposure through use of engineering controls, proper respiratory protection, or an SCBA (AAR, 2002; Pohanish, 2002).
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 100-66-3.
ENGINEERING CONTROLS
- Engineering controls should be implemented whenever feasible to control exposure to anisole to below assigned limits (Pohanish, 2002).
- Safe work practices may include use of closed systems, local exhaust ventilation, or other engineering controls. Explosion-proof electrical equipment should be used where potential for temperatures above the flash point may exist ((NIOSH ICSC, 2001)).
OTHER
- INDUSTRIAL DECONTAMINATION
In case of bodily contact, eyes and body should be immediately and thoroughly washed with water or soap and water for at least 15 minutes. Contaminated clothing and shoes should be removed and isolated at the site (AAR, 2002). Emergency showers and eyewash stations should be available near any area where anisole is used, handled, or stored (Pohanish, 2002).
-PHYSICAL HAZARDS
FIRE HAZARD
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS100-66-3 (NFPA, 2002):
Listed as: Anisole Flammability Rating: 2
- INITIATING OR CONTRIBUTING PROPERTIES
Flames, sparks, or any other source of ignition should be kept away from anisole due to fire and explosion hazards. In addition, explosive mixtures may form in air (AAR, 2002; (NIOSH ICSC, 2001)).
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
CAUTION: All these products have a very low flash point: Use of water spray when fighting fire may be inefficient. CAUTION: For mixtures containing a high percentage of an alcohol or polar solvent, alcohol-resistant foam may be more effective.
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004)
Water spray, fog or regular 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 128 (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 CAS100-66-3 (NFPA, 2002):
- Alcohol foam, dry chemical (powder), or carbon dioxide extinguishers should be used for fire control. Water may be applied at a safe distance to keep drums/containers cool. Water as fog or spray also may be used to knock down vapors. Solid streams of water, however, may be ineffective for extinguishing fires. Run-off water should be prevented from entering sewers and waterways (AAR, 2002; Lewis, 2000; (NIOSH ICSC, 2001); Pohanish, 2002).
EXPLOSION HAZARD
- Anisole can form explosive mixtures in air. The vapor/air explosion hazard increases at temperatures above 52 degrees C (125 degrees F) ((NIOSH ICSC, 2001)).
Above 52 degrees C, a closed system, ventilation, and explosion-proof equipment should be used when handling anisole ((NIOSH ICSC, 2001)).
- Containers should be cooled with water spray or by flooding with water in the event of a fire as heated containers may explode (AAR, 2002; (NIOSH ICSC, 2001); Pohanish, 2002).
- An explosion hazard is associated with anisole vapors in a confined space if fire enters the area. A confined space containing anisole vapors should be monitored for explosive levels prior to entry (Pohanish, 2002).
DUST/VAPOR HAZARD
- Anisole vapors can be moderately toxic and inhalation should be avoided. Anisole vapors can irritate the eyes, respiratory tract, and skin (AAR, 2002; Lewis, 2000; Pohanish, 2002).
- Anisole vapors are heavier than air and may travel along the ground to ignition sources and flashback. Vapors may collect in low lying areas. An explosion may occur when vapors in a confined space come into contact with fire (AAR, 2002; Pohanish, 2002).
REACTIVITY HAZARD
- Contact with strong acids or strong oxidizing agents may produce an incompatible chemical reaction ((NIOSH ICSC, 2001); Pohanish, 2002).
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 128 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (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 128 (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.
- Persons not in PPE should be evacuated from the area of a spill or leak (Pohanish, 2002).
- During container cooling in a fire situation, the area should be immediately evacuated if an increasing rising sound is emitted from container venting safety devices or if container deformation or discoloration occurs (Pohanish, 2002).
- AIHA ERPG Values for CAS100-66-3 (AIHA, 2006):
- DOE TEEL Values for CAS100-66-3 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Anisole; (Anisole anhydrous; Methoxybenzene) TEEL-0 (units = mg/m3): 4 TEEL-1 (units = mg/m3): 12.5 TEEL-2 (units = mg/m3): 75 TEEL-3 (units = mg/m3): 400 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 CAS100-66-3 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS100-66-3 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (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 128 (ERG, 2004) The following actions can be implemented in the event of a spill: (AAR, 2002; Pohanish, 2002) All cleanup personnel should wear appropriate PPE. Evacuate personnel not wearing PPE until cleanup is finished. Avoid inhalation or bodily contact. Remove or keep any ignition sources away from the spill area. Stay upwind. Ventilate spill area. Prevent spill from entering sewers and waterways.
In the event of a spill, ventilation should be implemented and all ignition sources removed. Spilled material should be collected and placed in sealed containers. Used absorbent material should also be containerized and removed ((NIOSH ICSC, 2001)).
All persons in spill area must wear appropriate PPE. Remove all potential ignition sources from the immediate area. Ventilate the spill area. Fly ash, cement powder, or similar commercial sorbents can be used to absorb liquid anisole. Collect leaking liquid and used absorbent in sealable containers (AAR, 2002; Pohanish, 2002). Trapped material can be removed with suction hoses in small water spills (AAR, 2002).
LARGE SPILL PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 128 (ERG, 2004) LAND SPILL (Pohanish, 2002; AAR, 2002) -- Prevent spill flow from entering sewers or waterways. Contain or control spill through use of dikes, storage pits, sand bags, foamed polyurethane, foamed concrete, or similar means. Use water spray to disperse vapors. Use dry earth, sand, fly ash, cement powder, or a similar inert commercial sorbent to absorb bulk liquid anisole. Collect leaking liquid and place used absorbent material in sealable containers for disposal.
WATER SPILL (AAR, 2002) AIR RELEASE (AAR, 2002; Pohanish, 2002) -- Media or material contaminated by cleanup may need to be managed as a hazardous waste and disposed appropriately according to environmental regulations (Pohanish, 2002).
Incineration is a suggested disposal method (Pohanish, 2002). Waste management activities associated with material disposition are unique to individual situations. Proper waste characterization and decisions regarding waste management should be coordinated with the appropriate local, state, or federal authorities to ensure compliance with all applicable rules and regulations.
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Anisole may be formed anthropogenically or naturally as a product of hydrocarbon combustion. Anisole has been detected in water from river basins in heavily populated areas of Germany, Spain, and China. Anisole has also been detected in lakes that received ash fallout from the Mount St. Helens eruption (HSDB, 2003).
- Anisole may be released to the environment through its industrial manufacture, transport, and disposal; through its use in the manufacture of other organic chemicals, such as fragrances and pharmaceuticals; or through its use as a solvent or heat transfer medium. Anisole has been detected in waste water from the following industries (HSDB, 2003):
organics and plastics industry organic chemical industry holding ponds from olive oil production wastewater from coal gasification plants raw wastewater and dye effluent from a dye manufacturing plant
- Common exposure routes to anisole for the general public include meat ingestion and inhalation of exhaust fumes from automobiles or kerosene space heaters. Anisole concentrations in gasoline exhaust are generally less than 0.1 ppm. Common routes for occupational exposure include inhalation and dermal contact (Verschueren, 2001; HSDB, 2003).
ENVIRONMENTAL FATE AND KINETICS
In the atmosphere, vapor-phase anisole reacts with photochemically-produced hydroxyl radicals (atmospheric concentration is 5x10(+5) hydroxyl radicals per cubic cm; estimated half-life is 22 hours). Anisole can be washed out of the atmosphere by rain (HSDB, 2003).
SURFACE WATER Anisole may be readily lost by volatilization in aquatic systems. Anisole is sensitive to oxidation by hydroxyl radicals in water, particularly under conditions of sunlight and clear water (i.e., relatively free of humic materials and other hydroxyl radical scavengers). One older (1964) Russian study reported anisole as stable in water for 4 days (HSDB, 2003). Estimated volatilization half-lives for anisole in aquatic systems include: 3.2 hours for a model river (1 m deep, flowing 1 m/s, wind speed 3 m/s) and 4.2 days for a model lake (1 m deep, flowing 0.05 m/sec, wind speed 0.5 m/sec) (HSDB, 2003) .
TERRESTRIAL Anisole is considered highly mobile, readily leachable and readily capable of volatilizing from both dry and moist soil (based on physicochemical values including Koc, Henry's Law constant, vapor pressure) (HSDB, 2003) .
ABIOTIC DEGRADATION
- Anisole is very mobile in the environment. It does not generally adsorb to soil and will likely leach from soil or volatilize to the atmosphere. It will readily volatilize from aquatic systems. It may undergo biodegradation in water and soil, and is not highly bioconcentrated. In the atmosphere, anisole exists as a vapor and may be removed through photochemical reaction with hydroxyl radicals or by wet deposition (HSDB, 2003).
BIODEGRADATION
Screening tests show anisole is readily biodegradable in soil. Decomposition by soil microflora can occur in 8 days (Verschueren, 2001). Anisole was completely degraded in a biodegradation study when soil inoculum was used (HSDB, 2003) .
Screening tests show anisole is readily biodegradable in water and likely to biodegrade in natural water systems (HSDB, 2003) . Anisole water concentrations were reduced by approximately 93% in a model aquatic ecosystem study using fish, larvae, algae, Daphnia, and snails (test conditions: 24 hours duration, 26.7 degrees C, 12 hours simulated daylight exposure; degradation products were detected) (HSDB, 2003).
In a 2-week biodegradation screening test using anisole (100 ppm) and an activated sludge inoculum, 56% BOD (biological oxygen demand) was reported. In a similar biodegradation test, more than 70% DOC (dissolved organic carbon) and 60% BOD were reported (HSDB, 2003).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Anisole is a mobile liquid that possesses an aromatic, agreeable, anise-like odor and a clear to yellowish, straw color (HSDB, 2003; Budavari, 2001; Lewis, 2000; Sittig, 1991).
VAPOR PRESSURE
- 3.1 mmHg (at 25 degrees C) (Verschueren, 2001)
- 0.47 kPa (at 25 degrees C) ((NIOSH ICSC, 2001))
- 3.54 mmHg (0.472 kPa) (at 25 degrees C) (HSDB, 2003)
- 10 mmHg (at 42 degrees C) (Verschueren, 2001)
- 10 mmHg (at 42.2 degrees C) (Lewis, 2000; ILO, 1998)
- 40 mmHg (at 70 degrees C) (Verschueren, 2001)
SPECIFIC GRAVITY
- NORMAL TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
0.9701 (at 45/4 degrees C) (Budavari, 2001) 0.99 (at 20/4 degrees C) (Verschueren, 2001) 0.9956 (at 18/4 degrees C) (Budavari, 2001) 0.999 (at 15/15 degrees C) (Lewis, 2001)
- TEMPERATURE AND/OR PRESSURE NOT LISTED
0.95 - 1.0 (water=1) (NFPA, 2002) 0.983 - 0.988 (Lewis, 2000) 0.99 (water=1) ((NIOSH ICSC, 2001)) 0.9961 (water=1) (ILO, 1998)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
vapor air mixture: 1.13 (at 20 degrees C) (air=1) ((NIOSH ICSC, 2001)) 3.7 (air=1) (NFPA, 2002; (NIOSH ICSC, 2001)) 3.72 (air=1) (Verschueren, 2001; Lewis, 2000; ILO, 1998)
FREEZING/MELTING POINT
-37.4 degrees C (at 760 mmHg) (Bingham et al, 2001) -37.3 degrees C (Budavari, 2001; Lewis, 2000) -37 degrees C (Ashford, 2001; Verschueren, 2001)
BOILING POINT
- 5.4 degrees C (at 1 mmHg) (Budavari, 2001)
- 30.0 degrees C (at 5 mmHg) (Budavari, 2001)
- 42.2 degrees C (at 10 mmHg) (Budavari, 2001)
- 55.8 degrees C (at 20 mmHg) (Budavari, 2001)
- 70.7 degrees C (at 40 mmHg) (Budavari, 2001)
- 93.0 degrees C (at 100 mmHg) (Budavari, 2001)
- 153.8 degrees C (Verschueren, 2001; Lewis, 2000)
- 307 degrees F (AAR, 2002)
- 154 degrees C, 309 degrees F (at 760 mm Hg) (NFPA, 2002; Bingham et al, 2001)
- 155 degrees C (ILO, 1998)
- 155.5 degrees C (at 760 mm Hg) (Budavari, 2001)
FLASH POINT
- 51.6 degrees C; 125 degrees F (open cup) (Lewis, 2001)
- 52 degrees C; 125 degrees F (open cup) (NFPA, 2002; (NIOSH ICSC, 2001))
- 125 degrees F (AAR, 2002)
AUTOIGNITION TEMPERATURE
- 475 degrees C; 887 degrees F (NFPA, 2002; (NIOSH ICSC, 2001); Lewis, 2000; ILO, 1998)
SOLUBILITY
Insoluble (Ashford, 2001; Budavari, 2001; Lewis, 2001; Lewis, 2000) Poor solubility in water ((NIOSH ICSC, 2001)) 143 mg/L 1520 mg/L 10,400 mg/L
Acetone: very soluble (HSDB, 2003) Alcohol: soluble (Budavari, 2001; Lewis, 2001; Lewis, 2000) Ether: soluble (Budavari, 2001; Lewis, 2001; Lewis, 2000) Oxygenated solvents: soluble (Ashford, 2001)
OCTANOL/WATER PARTITION COEFFICIENT
- log Kow = 2.11 (HSDB, 2003; (NIOSH ICSC, 2001))
HENRY'S CONSTANT
- 4.35 x 10(-3) atm-cu-m/mol (estimated using fragment constant method) (HSDB, 2003)
SPECTRAL CONSTANTS
OTHER/PHYSICAL
- ORGANIC CARBON PARTITION COEFFICIENT
Koc = 35 (experimental) (HSDB, 2003) Koc = 118 (estimated based on molecular connectivity indices) (HSDB, 2003)
34.15 dyne/cm (at 30 degrees C) (HSDB, 2003) 35.00 dyne/cm (at 20 degrees C) (HSDB, 2003) 36.18 dyne/cm (at 15 degrees C) (HSDB, 2003)
1.513 - 1.518 (Lewis, 2000) 1.5170 (at 20 degrees C) (Lewis, 2001) 1.51791 (at 20 degrees C and sodium light) (Budavari, 2001)
- NUCLEAR MAGNETIC RESONANCE
0.778 cP (at 30 degrees C) (HSDB, 2003) 1.52 cP (at 15 degrees C) (HSDB, 2003)
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