MONOMETHYL ANILINE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
MONOMETHYL ANILINE ANILINOMETHANE ANILINE, N-METHYL BENZENAMINE, N-METHYL- (METHYLAMINO) BENZENE N-METHYLAMINOBENZENE METHYLANILINE METHYLANILINE (MONO) N-METHYLANILINE N-METHYLBENZENAMINE METHYLPHENYLAMINE N-METHYLPHENYLAMINE MONOMETHYLANILINE N-MONOMETHYLANILINE N-PHENYLMETHYLAMINE
IDENTIFIERS
SYNONYM REFERENCE
- (CHRIS , 1997; HSDB , 1997; RTECS , 1997)
USES/FORMS/SOURCES
The compound is produced naturally and can be found in spinach, red cabbage, carrots, celery, and other fresh vegetables (HSDB , 1997). The compound can be made by heating methyl alcohol and aniline chloride under pressure (Budavari, 1996).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- No reports of human poisoning with n-methyl aniline were found in available references at the time of this review. Clinical toxicity is expected to resemble that seen in cases of ANILINE poisoning. Overexposure may produce methemoglobinemia, with cyanosis, weakness, dizziness, severe headache, and formation of Heinz bodies.
- Symptoms may also include cardiac effects (arrhythmias, shock, heart block), painful micturition, hematuria, hemoglobinuria, oliguria, renal insufficiency, nausea, vomiting, confusion, tinnitus, disorientation, lethargy, convulsions, coma, and death due to cardiovascular collapse and respiratory paralysis.
- Experimental animals have died from pulmonary involvement including pulmonary edema, interstitial pneumonia, and occasional centrilobular hepatic necrosis and moderate kidney damage.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
TOXIC; inhalation, ingestion or skin contact with material may cause severe injury or death. Contact with molten substance may cause severe burns to skin and eyes. Avoid any skin contact. Effects of contact or inhalation may be delayed. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance; give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. 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. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. 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.
FIRST AID 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. Because of the potential for rapid onset of CNS depression or seizures with possible aspiration of gastric contents, 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. A number of chemicals produce abnormalities of the hematopoietic system, liver, and kidneys. Monitoring complete blood count, urinalysis, and liver and kidney function tests is suggested for patients with significant exposure.
INHALATION EXPOSURE - INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm. If bronchospasm and wheezing occur, consider treatment with inhaled sympathomimetic agents. ACUTE LUNG INJURY: Maintain ventilation and oxygenation and evaluate with frequent arterial blood gases and/or pulse oximetry monitoring. Early use of PEEP and mechanical ventilation may be needed. SEIZURES: Administer a benzodiazepine; DIAZEPAM (ADULT: 5 to 10 mg IV initially; repeat every 5 to 20 minutes as needed. CHILD: 0.1 to 0.5 mg/kg IV over 2 to 5 minutes; up to a maximum of 10 mg/dose. May repeat dose every 5 to 10 minutes as needed) or LORAZEPAM (ADULT: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist. CHILD: 0.05 to 0.1 mg/kg IV over 2 to 5 minutes, up to a maximum of 4 mg/dose; may repeat in 5 to 15 minutes as needed, if seizures continue). Consider phenobarbital or propofol if seizures recur after diazepam 30 mg (adults) or 10 mg (children greater than 5 years). Monitor for hypotension, dysrhythmias, respiratory depression, and need for endotracheal intubation. Evaluate for hypoglycemia, electrolyte disturbances, and hypoxia.
METHEMOGLOBINEMIA: Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy. METHYLENE BLUE: INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules and 10 mg/1 mL (1% solution) vials. Additional doses may sometimes be required. Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection. NEONATES: DOSE: 0.3 to 1 mg/kg. Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome.
DERMAL EXPOSURE - DECONTAMINATION: Remove contaminated clothing and jewelry and place them in plastic bags. Wash exposed areas with soap and water for 10 to 15 minutes with gentle sponging to avoid skin breakdown. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999). Treat dermal irritation or burns with standard topical therapy. Patients developing dermal hypersensitivity reactions may require treatment with systemic or topical corticosteroids or antihistamines. METHEMOGLOBINEMIA: Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy. METHYLENE BLUE: INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules and 10 mg/1 mL (1% solution) vials. Additional doses may sometimes be required. Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection. NEONATES: DOSE: 0.3 to 1 mg/kg. Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome.
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 - Because of the potential for CNS depression or seizures, do not induce emesis. GASTRIC LAVAGE: Consider after ingestion of a potentially life-threatening amount of poison if it can be performed soon after ingestion (generally within 1 hour). Protect airway by placement in the head down left lateral decubitus position or by endotracheal intubation. Control any seizures first. ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old. SEIZURES: Administer a benzodiazepine; DIAZEPAM (ADULT: 5 to 10 mg IV initially; repeat every 5 to 20 minutes as needed. CHILD: 0.1 to 0.5 mg/kg IV over 2 to 5 minutes; up to a maximum of 10 mg/dose. May repeat dose every 5 to 10 minutes as needed) or LORAZEPAM (ADULT: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist. CHILD: 0.05 to 0.1 mg/kg IV over 2 to 5 minutes, up to a maximum of 4 mg/dose; may repeat in 5 to 15 minutes as needed, if seizures continue). Consider phenobarbital or propofol if seizures recur after diazepam 30 mg (adults) or 10 mg (children greater than 5 years). Monitor for hypotension, dysrhythmias, respiratory depression, and need for endotracheal intubation. Evaluate for hypoglycemia, electrolyte disturbances, and hypoxia.
METHEMOGLOBINEMIA: Determine the methemoglobin concentration and evaluate the patient for clinical effects of methemoglobinemia (ie, dyspnea, headache, fatigue, CNS depression, tachycardia, metabolic acidosis). Treat patients with symptomatic methemoglobinemia with methylene blue (this usually occurs at methemoglobin concentrations above 20% to 30%, but may occur at lower methemoglobin concentrations in patients with anemia, or underlying pulmonary or cardiovascular disorders). Administer oxygen while preparing for methylene blue therapy. METHYLENE BLUE: INITIAL DOSE/ADULT OR CHILD: 1 mg/kg IV over 5 to 30 minutes; a repeat dose of up to 1 mg/kg may be given 1 hour after the first dose if methemoglobin levels remain greater than 30% or if signs and symptoms persist. NOTE: Methylene blue is available as follows: 50 mg/10 mL (5 mg/mL or 0.5% solution) single-dose ampules and 10 mg/1 mL (1% solution) vials. Additional doses may sometimes be required. Improvement is usually noted shortly after administration if diagnosis is correct. Consider other diagnoses or treatment options if no improvement has been observed after several doses. If intravenous access cannot be established, methylene blue may also be given by intraosseous infusion. Methylene blue should not be given by subcutaneous or intrathecal injection. NEONATES: DOSE: 0.3 to 1 mg/kg. Concomitant use of methylene blue with serotonergic drugs, including serotonin reuptake inhibitors (SRIs), selective serotonin reuptake inhibitors (SSRIs), serotonin and norepinephrine reuptake inhibitors (SNRIs), tricyclic antidepressants (TCAs), norepinephrine-dopamine reuptake inhibitors (NDRIs), triptans, and ergot alkaloids may increase the risk of potentially fatal serotonin syndrome.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
In rabbits, the minimum lethal oral dose of monomethyl aniline is 280 mg/kg (ACGIH, 1991). When administered intravenously, the minimum lethal dose for rabbits and cats is 24 mg/kg (ACGIH, 1991). Percutaneous administration to rabbits at 3 grams or more per kg of body weight for 1 hour or more was always fatal (ACGIH, 1991). Rabbits, guinea pigs, and rats died after inhalational exposure to an airborne concentration of 7.6 ppm for 130 or fewer 7-hour periods. Death in cats occurred after exposure to an airborne concentration of 27 ppm for 58 or fewer 7-hour periods (ACGIH, 1991).
MAXIMUM TOLERATED EXPOSURE
At the time of this review, no specific maximum tolerated exposure information was found. Exposure may produce symptoms including weakness, dizziness, headache, dyspnea, cyanosis, methemoglobinemia, pulmonary edema, and liver and kidney damage (NIOSH , 1997).
A dog survived 50 7-hour inhalation exposures to an airborne concentration of 7.6 ppm of monomethyl aniline, a monkey survived 130 such exposures at an airborne concentration of 2.4 ppm, and a rabbit survived 130 exposures at an airborne concentration of 2.3 ppm (ACGIH, 1991).
- Carcinogenicity Ratings for CAS100-61-8 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: N-Methyl aniline EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Monomethyl aniline 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 CAS100-61-8 (U.S. Environmental Protection Agency, 2011):
References: ITI, 1988 Lewis, 1996 RTECS, 1997 Note: All values are from RTECS (1997), unless otherwise noted.
CALCULATIONS
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS100-61-8 (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 CAS100-61-8 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS100-61-8 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS100-61-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS100-61-8 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS100-61-8 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS100-61-8 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS100-61-8 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS100-61-8 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS100-61-8 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS100-61-8 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS100-61-8 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2294 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2294 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS100-61-8 (NFPA, 2002):
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Store monomethyl aniline in a cool, well-ventilated area, out of direct sunlight and away from open flames (ITI, 1988).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
EYE/FACE PROTECTION
- Wear appropriate goggles and protective clothing (AAR, 1994).
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 100-61-8.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) Combustible material: may burn but does not ignite readily. When heated, vapors may form explosive mixtures with air: indoors, outdoors and sewers explosion hazards. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Contact with metals may evolve flammable hydrogen gas. Containers may explode when heated. Runoff may pollute waterways. Substance may be transported in a molten form.
Monomethyl aniline is combustible (Lewis, 1993). ITI (1988) states that the compound is flammable and, when heated slightly, will catch fire; however, AAR (1994) maintains that monomethyl aniline "does not burn or burns with difficulty."
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS100-61-8 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Dry chemical, CO2, alcohol-resistant foam or water spray. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. 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.
- NFPA Extinguishing Methods for CAS100-61-8 (NFPA, 2002):
- To extinguish fire, use water in flooding amounts as fog (AAR, 1994). CHRIS (1997), however, warns that water may not be effective in putting out fire.
- Use foam, carbon dioxide, or dry chemical (AAR, 1994).
DUST/VAPOR HAZARD
- Inhalation of monomethyl aniline is a potential health hazard (NIOSH , 1997).
- Avoid breathing vapors (AAR, 1994). Wear appropriate respirator (ITI, 1988).
REACTIVITY HAZARD
- Monomethyl aniline can react with oxidizing materials and strong acids (HSDB, 2004).
- The compound may attack some types of plastics (CHRIS , 1997).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (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 153 (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 in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate enclosed areas.
- AIHA ERPG Values for CAS100-61-8 (AIHA, 2006):
- DOE TEEL Values for CAS100-61-8 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Methylaniline, n- TEEL-0 (units = ppm): 2 TEEL-1 (units = ppm): 2 TEEL-2 (units = ppm): 2.5 TEEL-3 (units = ppm): 100 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 CAS100-61-8 (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 CAS100-61-8 (National Institute for Occupational Safety and Health, 2007):
IDLH: 100 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
Spread a 9:1 mixture of sand and soda ash over a monomethyl aniline spill. Mix and transfer to a paper carton. Fill remainder of paper carton with ruffled paper and burn in a furnace with an afterburner and scrubber (ITI, 1988). Keep the substance from leaking into sewers and water sources. Build dikes, if necessary (AAR, 1994).
Dissolve monomethyl aniline in a combustible solvent such as alcohol or benzene. Spray the mixture into a furnace with an afterburner and scrubber (ITI, 1988). 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.
In an activated sludge test, 100 ppm of monomethyl aniline was moderately biodegradable, with 42% of total organic carbon removed (HSDB, 2004). The compound was biodegraded by Alcalignes sp. and Corynebacterium sp., both isolated from activated sludge in a semi-continuous activated sludge biodegradation test (HSDB, 2004). In a 3-week biodegradation study using an acclimated activated sludge inoculum, 99.9% degradation and 82% mineralization were achieved. When acclimation was performed in a single flask, biodegradation was quicker than by an enrichment method (HSDB, 2004). Standard aerobic biodegradability test results for monomethyl aniline include the following: in the Zahn-Wellens test, 92% dissolved organic carbon (DOC) in 8 days; in the French AFNOR test, 29% and 67% DOC removal after 28 and 42 days, respectively; in the Sturm test, after 14 days acclimation, 46% CO2 produced and 92% DOC removed in 28 days; in the OECD Screening test 17% DOC was removed after 19 days; in a 5-day test, 38% theoretical BOD was obtained; in a respiratory test that utilized 500 ppm of the test substance, and after 5 to 8 days, 18 to 20 theoretical BOD was expended; in a 30-day test with a drop of sewage as inoculum, 0% BOD was obtained; in the MITI test, 3% BODT was obtained in 14 days; and in a 21-day test using an activated sludge inoculum, 8% mineralization to CO2 occurred (HSDB, 2004). Under anaerobic conditions, using an anaerobic digesting sludge inoculum, the compound showed no potential for biodegradation (HSDB, 2004). The chemical degraded fairly quickly after being applied in sludge to soil. The sludge was dried and tilled 6 inches into the soil over 5 days. Five, 122, and 241 days after sludge application, the average concentration of the chemical in 3 plots in 0- to 6-inch cores was 511, 138, and 16 ppb, respectively. In 9- to 15-inch cores, 82 ppb was found 5 days after application; however, at later sampling dates, none was found (HSDB, 2004).
Spread a 9:1 mixture of sand and soda ash over a monomethyl aniline spill. Mix and transfer to a paper carton. Fill remainder of paper carton with ruffled paper and burn in a furnace with an afterburner and scrubber (ITI, 1988). "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" (HSDB, 2004).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Facilities that use incinerators may release monomethyl aniline to the environment, as the compound is found in incinerator waste streams (HSDB, 2004).
- The compound also may be released to the environment in tar wastes or emissions from coal gasification plants (HSDB, 2004).
ENVIRONMENTAL FATE AND KINETICS
Monomethyl aniline should exist in the air as vapor. While in the vapor phase or in aerosols it may photolyze or oxidize. Vapor phase photolysis rates are not known (HSDB, 2004). Its estimated half-life in air is 8.8 hours (HSDB, 2004).
SURFACE WATER Monomethyl aniline is sensitive to photooxidation and oxidation and may photodegrade in surface water or may be oxidized in water bodies by naturally occurring oxidants (HSDB, 2004). Some of the monomethyl aniline molecule is ionized at the acidic end of the pH range. This is based on a pKa for the compound of 4.848 at 25 degrees C. It is likely to oxidize and photo-oxidize in solution (HSDB, 2004). Based on an estimated Henry's Law constant of 1.14X10-5 atm-m(3)/mol, monomethyl aniline's half-life is expected to be 3.5 and 28 days in a model river and a model lake, respectively (HSDB, 2004).
TERRESTRIAL Monomethyl aniline does not adsorb well to soil. When released to soil, especially sandy soil, the compound may leach. It may photodegrade or volatilize from the soil surface (HSDB, 2004). A predicted Koc for monomethyl aniline from its molecular structure is 65. This indicates that the compound will be very mobile in soil; however, it reacts very slowly with humic material (HSDB, 2004).
ABIOTIC DEGRADATION
- Monomethyl aniline should exist in the air as vapor. While in the vapor phase or in aerosols it may photolyze or oxidize. Monomethyl aniline is sensitive to photooxidation and oxidation and may photodegrade in surface water or may be oxidized in water bodies by naturally occurring oxidants. Monomethyl aniline does not adsorb well to soil. When released to soil, especially sandy soil, the compound may leach, or photodegrade or volatilize from the soil surface. Monomethyl aniline bioconcentrates at a very low level in fish (HSDB, 2004).
BIODEGRADATION
- Studies show Nitrosomonas can inhibit biodegradation by approximately 50% to 90% at concentrations of <1 mg/L to 100 mg/L, respectively (Verschueren, 2001).
- In an activated sludge test, 100 ppm of monomethyl aniline was moderately biodegradable, with 42% of total organic carbon removed (HSDB, 2004).
- Under anaerobic conditions, using an anaerobic digesting sludge inoculum, the compound showed no potential for biodegradation (HSDB, 2004).
- The chemical degraded fairly quickly after being applied in sludge to soil. The sludge was dried and tilled 6 inches into the soil over 5 days. Five, 122, and 241 days after sludge application, the average concentration of the chemical in 3 plots in 0- to 6-inch cores was 511, 138, and 16 ppb, respectively. In 9- to 15-inch cores, 82 ppb was found 5 days after application; however, at later sampling dates, none was found (HSDB, 2004).
BIOACCUMULATION
Monomethyl aniline bioconcentrates at a very low level in fish. (This is based on procedures developed by the Ministry of International Trade and Industry in Japan.) An estimated BCF of 11 based on a log Kow of 1.66 indicates that the chemical will not bioconcentrate in aquatic organisms (HSDB, 2004).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Monomethyl aniline is a colorless to slightly yellow liquid. Upon exposure to air, it turns brown (Budavari, 1996).
- It possesses a weak, ammoniacal odor (NIOSH , 1997).
VAPOR PRESSURE
- 0.3 mmHg (at 20 degrees C) (ACGIH, 1991)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
- TEMPERATURE AND/OR PRESSURE NOT LISTED
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
BOILING POINT
- 194-196 degrees C (Budavari, 1996)
- 190-191 degrees C (Lewis, 1993)
FLASH POINT
- 175 degrees F (NIOSH , 1997)
- 79.4 degrees C (closed cup) (Clayton & Clayton, 1994)
EXPLOSIVE LIMITS
SOLUBILITY
It is soluble in alcohol, ether, and oxygenated solvents (Budavari, 1996; Ashford, 1994).
OCTANOL/WATER PARTITION COEFFICIENT
- log kow = 1.66 (HSDB , 1997)
HENRY'S CONSTANT
- 1.14x10-5 atm m(3)/mol (estimated) (HSDB , 1997)
OTHER/PHYSICAL
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