METHYL METHACRYLATE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
METHYL METHACRYLATE ACRYLIC ACID, 2-METHYL-, METHYL ESTER DIAKON METAKRYLAN METYLU (Polish) METHACRYLATE DE METHYLE (French) METHACRYLIC ACID, METHYL ESTER METHACRYLSAEUREMETHYL ESTER (German) METHYLESTER KYSELINY METHAKRYLOVE (Czech) METHYLMETHACRYLAAT (Dutch) METHYL-METHACRYLAT (German) METHYL METHACRYLATE MONOMER METHYL METHACRYLATE MONOMER, INHIBITED METHYL METHACRYLATE MONOMER, UNINHIBITED METHYL METHYLACRYLATE METHYL alpha-METHYLACRYLATE METHYL 2-METHYL-2-PROPENOATE METYYL 2-METHYLPROPENOATE 2-METHYL-2-PROPENOIC ACID METHYL ESTER 2-(METHOXYCARBONYL)-1-PROPENE METIL METACRILATO (Italian) MMA MME MONOCITE METHACRYLATE MONOMER PEGALAN 2-PROPENOIC ACID, 2-METHYL-, METHYL ESTER "MONOCITE" METHYACRYLATE MONOMER 50N METHACRYLATE MONOMER METHYL ESTER OF METHACRYLIC ACID MMA (METHYL METHACRYLATE) MME (METHYL METHACRYLATE) ST 1
IDENTIFIERS
1247-Methyl methacrylate monomer, stabilized 1247-Methyl methacrylate monomer, inhibited
4907255 - Methyl methacrylate monomer, uninhibited 4907250 - Methyl methacrylate monomer, inhibited
129-FLAMMABLE LIQUIDS (POLAR / WATER-MISCIBLE / NOXIOUS)(for UN/NA Number1247) Polymerization Hazard (ERG, 2004)
SYNONYM REFERENCE
- (HSDB , 2000; RTECS , 2000)
USES/FORMS/SOURCES
Methyl methacrylate is used in the production of acrylics, clear plastics, marble-like surfaces (for kitchens and baths), extrusion powders, paints and inks, adhesive cements, industrial flooring compositions, precast concrete composites, resin mortars, polishes, dental fillers and cements, and surgical implants (ACGIH, 1999; (Woolf & Shaw, 1998; Gesell & Stephen, 1997; Ashford, 1994; Clayton & Clayton, 1994; Hathaway et al, 1996; Lewis, 1997; Raffle et al, 1994).
It is a flammable, clear, colorless liquid; its odor has been described as distinctive, fruity, ester-like, acrid, and pungent. Methyl methacrylate monomer is a polymerization hazard when exposed to light, heat, oxygen, or ionizing radiation. It is usually found as a commercial or technical grade (99.8% pure) which contains inhibitors to prevent polymerization (AAR, 1998; ACGIH, 1999; (Ashford, 1994; Clayton & Clayton, 1994; ILO, 1998; Lewis, 1996; Lewis, 1997; Lewis, 1997; Verschueren, 1983).
Methyl methacrylate may be produced by alcoholysis (methanol + methacrylamide), by esterification (methanol + methacrylic acid), by the combination of acetone cyanohydrin, methanol, and dilute sulfuric acid, and by the oxidation of tert-butyl alcohol to methacrolein and then to methacrlic acid followed by reaction with methanol (Ashford, 1994; Clayton & Clayton, 1994; Lewis, 1997).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- USES: Methyl methacrylate is used in the production of acrylics, clear plastics, marble-like surfaces, extrusion powders, paints and inks, adhesive cements, industrial flooring compositions, precast concrete composites, resin mortars, polishes, dental fillers, surgical implants, and bone cements.
- TOXICOLOGY: Methyl methacrylate decreases the amplitude of the action potential in peripheral nerves by causing lysis of membrane lipids and destruction of the myelin sheath. It is an irritant and sensitizer, and can cause bronchospasm and dermatitis. At high concentrations, it has CNS and respiratory depressant effects. It is thought to promote granuloma formation and trigger focal bone resorption.
- EPIDEMIOLOGY: Exposure to liquid methyl methacrylate is generally occupational. It is usually found as a commercial or technical grade (99.8% pure) which contains inhibitors such as hydroquinone or monomethyl ether of hydroquinone to prevent polymerization. Once polymerized, it is inert.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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
- Methyl methacrylate is moderately irritating to the eyes, skin, and respiratory tract. Ocular exposure in rabbits has resulted in corneal irritation which lasted for several days (Clayton & Clayton, 1994) Hathaway, 1991; (Sax & Lewis, 1989; NIOSH, 1976).
- A localized fibrin mass, damage to the corneal endothelium, and corneal swelling with partial vascularization developed acutely when 10 microliters of methyl methacrylate were injected into the anterior chamber of rabbit eyes. Anterior lens opacity and areas of iris atrophy developed in rabbit eyes previously instilled with MMA (Holyk & Eifrig, 1979).
- A dose-response relationship between olfactory dysfunction and cumulative exposure scores was noted in a cross-sectional study of volunteers working in a plant manufacturing several chemicals, among which were the methacrylates (Schwartz et al, 1989).
- Systemic vasodilation and hypotension have been reported following MMA use as a bone cement in total hip replacement surgical procedures (HSDB , 1996). Cardiac arrest and fat and bone marrow embolisms have been reported in this setting, and are presumably due to heat and pressure in the femoral canal while the MMA polymer is curing (Merin, 1983). A patient developed transient episodes of atrioventricular block on 2 occasions, 4 weeks apart, immediately after insertion of MMA cement into the femoral cavity (Brown & Parmley, 1982).
- MMA monomer has been shown to have a direct myocardial depressant effect on isolated perfused rabbit hearts (Mir et al, 1973; Wong et al, 1977).
- Occupational asthma has been associated with the use of various methyl methacrylate compounds (Pickering et al, 1986; Lozewicz et al, 1985). Respiratory depression has been seen following large MMA doses in experimental animals. Transient tachypnea has been seen after small doses (0.03 mL/kg intravenously) were given to experimental animals (Deichmann, 1941) RTECS, 1996). Atelectasis and emphysema were found in a rhesus monkey that died in coma after an accidental 22-hour exposure to MMA vapor (Kessler et al, 1977). Respiratory arrest and death have been described in acutely exposed experimental animals (ACGIH, 1991).
- Headache, irritability, and excitement may be noted (RTECS, 1996; (Sax & Lewis, 1989; Scolnick & Collins, 1986). Chronic paresthesias may also be noted, which outlast eruptions of allergic contact dermatitis (Pegum & Medhurst, 1971) Hathaway, 1991). Methyl methacrylate vapor is a central nervous system (CNS) depressant (ILO, 1983; Sax & Lewis, 1989; HSDB , 1996). Rats exposed to an airborne concentration of 400 ppm of MMA vapor for 60 minutes had a decreased neuronal firing rate (Innes & Tansy, 1981).
- Anorexia and nausea lasting for several hours were seen in dental students working with MMA (Tansy et al, 1974).
- Patients who underwent hip replacement with polymethyl methacrylate bone cement had transient, but dose-related, elevations of serum gammaglutamyl transferase (GGT) (Pople & Phillips, 1988). Experimental animals exposed to 25 mg of MMA twice weekly had decreases in serum glycoprotein and albumin levels and increases in other hepatic enzymes (Motoc et al, 1971). Centrilobular hepatic necrosis was found in a rhesus monkey that died after an accidental 22-hour vapor exposure (Gosselin et al, 1984).
- Unspecified kidney lesions have been produced in humans and experimental animals when MMA has been ingested (Lefaux, 1968; ACGIH, 1991).
- Allergic contact dermatitis has been reported (Foussereau et al, 1989; Pegum & Medhurst, 1971; Clayton & Clayton, 1994; HSDB , 1996). Other acrylic monomers may cross-react and produce a similar dermatitis (Fisher, 1980a; Lovell et al, 1985). Allergic contact dermatitis caused by MMA is characterized by paresthesias and tenderness that outlast the eruption (Ellenhorn & Barceloux, 1988).
- Pruriginous papulo-erythematous lesions with some degree of hyperkeratosis erupted near the amputation stump and spread to rest of the body (sparing the face and the scalp) after a man revarnished his lower leg prosthesis with methacrylates (Romaguera et al, 1989).
- Eczematous onychial and paronychial tissue reactions have been reported in patients using acrylic plastic artificial fingernails. Dystrophic nail changes may persist for years (Fisher, 1980) 1989, 1990).
- A 31-year-old nurse exposed to methyl methacrylate vapors developed diffuse erythroderma, dyspnea, headache, hypertension, lethargy, and lightheadedness (Scolnick & Collins, 1986).
CHRONIC CLINICAL EFFECTS
- Acute hypertension, erythroderma, and dyspnea developed in a nurse repeatedly exposed to a surgical cement containing 97 percent methyl methacrylate monomer (Scolnick & Collins, 1986).
- Dental technicians who molded methyl methacrylate putty with their bare hands had significantly slower distal sensory conduction velocities in the digits, implicating mild axonal degeneration in the area of MMA contact (Rajaniemi et al, 1989; Seppalainen & Rajaniemi, 1984).
- Artificial fingernail sculptors exposed to methyl methacrylate dusts and vapors consistently had more complaints of nasal and skin irritation, drowsiness, dizzy spells, and trembling of the hands, compared to controls (Hiipakka & Samimi, 1987).
- Contact stomatitis was reported in a 71-year-old woman who had a positive patch test to methyl methacrylate monomer extracted from her dentures which had been in use for 15 years and may have been incompletely polymerized (Kanzaki et al, 1989).
- Workers in plants manufacturing methyl methacrylate have complained of fatigue, headache, sleep disturbances, irritability, loss of memory, and pains in the extremities (ACGIH, 1991).
- In experimental animals, chronic exposure has caused renal cortical necrosis, tubular degeneration with focal mineralization, hepatic necrosis, central nervous system (CNS) depression, cerebellar congestion and hemorrhage, and death, apparently due to respiratory arrest (ACGIH, 1991).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
- Significant systemic toxicity is not expected after acute ingestion; gastrointestinal decontamination is generally not warranted.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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.
FIRST AID EYE EXPOSURE: Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Primary eye protection (spectacles or goggles), as defined by the Occupational Safety and Health Administration (OSHA) should be used when working with this chemical. Face shields should only be worn over primary eye protection. DERMAL EXPOSURE: Flush the contaminated skin with water promptly. If this chemical penetrates the clothing, immediately remove the clothing and flush the skin with water promptly. If irritation persists after washing, get medical attention. INHALATION EXPOSURE: Move the exposed person to fresh air at once. If breathing has stopped, perform artificial respiration. Keep the affected person warm and at rest. Get medical attention as soon as possible. ORAL EXPOSURE: If this chemical has been swallowed, get medical attention immediately. TARGET ORGANS: Eyes, skin and respiratory system (National Institute for Occupational Safety and Health, 2007; OSHA, 2000).
GENERAL Treatment is supportive. Monitor for hypotension and respiratory depression. 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.
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
-RANGE OF TOXICITY
MAXIMUM TOLERATED EXPOSURE
TLV-TWA: 50 ppm. NIOSH: TWA: 100 ppm (410 mg/m(3)); IDLH: 1000 ppm; OSHA PEL: 8-hour TWA: 100 ppm (410 mg/m(3)) (American Conference of Governmental Industrial Hygienists, 2010; U.S. Occupational Safety, and Health Administration (OSHA), 2010; National Institute for Occupational Safety and Health, 2007). TCLo (INHL) HUMAN: 125 ppm (RTECS , 2000) TCLo (INHL) HUMAN: 60 mg/m(3) (RTECS , 2000)
- Numbness, coldness, and paresthesia of the fingers have been reported among people who handle the monomer with their bare hands, most notably among dental technicians who mold methyl methacrylate putty. Allergic contact dermatitis as well as occupational asthma have been reported among workers who have been reexposed to methyl methacrylate liquid (ACGIH, 1999; (Hathaway et al, 1996; Raffle et al, 1994).
In a German study, an acute exposure of 20 healthy volunteers to 50 ppm of methyl methacrylate resulted in only minor irritation of the nasal mucosa, but no inflammatory changes in nasal epithelium and impairment of mucociliary transport or olfactory functioning were observed (Muttray et al, 2015). At concentrations of 0.5 to 50 parts per million, 78% of 152 exposed workers reported frequent headaches, 30% reported pain in the extremities, 10% reported irritability, 20% reported loss of memory, and 21% reported excessive fatigue and sleep disturbance (Blagodatin et al, 1976). At levels of 4 to 49 parts per million, workers in plants manufacturing polymethyl methacrylate sheets had no observable effects in terms of symptomatology and changes in blood pressure, respiratory function testing, hemoglobin and white blood count, urinalysis, and blood chemistry (Cromer J & Kronoveter K, 1976). With air levels from 3 to 77 parts per million, surgical assistants who mixed methyl methacrylate bone cement in operating rooms described occasional transient eye irritation (NIOSH, 1977). With exposures higher than 49 parts per million, statistically insignificant effects on serum glucose, blood urea nitrogen, cholesterol, albumin, and total bilirubin levels were noted among workers (Cromer J & Kronoveter K, 1976). 170 to 250 ppm causes irritation, 2300 ppm is intolerable (NIOSH, 1976). At concentrations of 100 to 599 mg/m(3), 75% of 300 exposed Soviet women developed irritability, fatigue, headache, and mucous membrane irritation (Dobrinsky, 1970). 150 mg/m(3) produce CNS effects when inhaled by humans (Gosselin et al, 1984).
- Carcinogenicity Ratings for CAS80-62-6 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: Methyl methacrylate EPA (U.S. Environmental Protection Agency, 2011): E ; Listed as: Methyl methacrylate 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: Methyl methacrylate 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: Methyl methacrylate 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 CAS80-62-6 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 1.4 mg/kg-day
Inhalation: Unit Risk: RfC: 7x10(-1) mg/m3
Drinking Water:
LC50- (INHALATION)MOUSE: LC50- (INHALATION)RAT: LCLo- (INHALATION)DOG: LCLo- (INHALATION)GUINEA_PIG: LCLo- (INHALATION)RABBIT: LD50- (ORAL)DOG: LD50- (SUBCUTANEOUS)DOG: LD50- (INTRAPERITONEAL)GUINEA_PIG: LD50- (ORAL)GUINEA_PIG: LD50- (SUBCUTANEOUS)GUINEA_PIG: LD50- (INTRAPERITONEAL)MOUSE: LD50- (ORAL)MOUSE: LD50- (SUBCUTANEOUS)MOUSE: LD50- (ORAL)RABBIT: LD50- (SKIN)RABBIT: LD50- (INTRAPERITONEAL)RAT: LD50- (ORAL)RAT: LD50- (SUBCUTANEOUS)RAT: LDLo- (SUBCUTANEOUS)CAT: LDLo- (INTRAVENOUS)DOG: LDLo- (SUBCUTANEOUS)RABBIT: 14 mL/kg -- Somnolence (general depressed activity); changes in lung, thorax, or respiration; hematuria (RTECS , 2000)
TCLo- (INHALATION)CAT: TCLo- (INHALATION)DOG: TCLo- (INHALATION)GUINEA_PIG: TCLo- (INHALATION)HAMSTER: TCLo- (INHALATION)HUMAN: 125 ppm -- Effect on sleep; Excitement; Anorexia (RTECS , 2000) 60 mg/m(3) -- Effects on sleep; Excitement; Blood pressure lowering not characterized in autonomic section (RTECS , 2000)
TCLo- (INHALATION)MOUSE: 41 g/m(3) for 90M for 15D- intermitent -- Death (RTECS , 2000) 5000 ppm for 6H for 14W- intermittent -- Other changes in sense organs and special senses (Nose, Eye, Ear, and Taste); Hepatitis (hepatocellular necrosis), zonal; Death (RTECS , 2000) 500 ppm for 6H for 2Y- intermittent -- Other changes in sense organs and special senses (Nose, Eye, Ear, and Taste); Fibrosis, focal (pneumoconiosis) (RTECS , 2000)
TCLo- (INHALATION)RABBIT: TCLo- (INHALATION)RAT: Female, 54 mg/m(3) for 24H at 8W prior to mating -- Menstrual cycle changes or disorders (RTECS , 2000) Female, 4480 mg/m(3) for 2H at 6-18D of pregnancy -- Post-implantation mortality (e.g., dead and or resorbed implants per total number of implants) (RTECS , 2000) Female, 109 g/m(3) for 17M at 6-15D of pregnancy -- Fetotoxicity (except death, e.g., stunted fetus); Developmental abnormalities in musculoskeletal system (RTECS , 2000) Female, 109 g/m(3) for 54M at 6-15D of pregnancy -- Fetal death; Other developmental abnormalities (RTECS , 2000) 116 ppm for 8H/D for 26W- intermittent -- Changes in serum composition (e.g., TP, bilirubin, cholesterol); Nutritional and Gross Metabolic (P); Effects on transaminases (RTECS , 2000) 1 mg/m(3) for 24H for 60D- continuous -- Muscle contraction or spasticity; Effect on true cholinesterase; Porphyrin including bile pigments (RTECS , 2000) 115 mg/m(3) for 3H for 17W- intermittent -- EKG changes not diagnostic of above; Other blood changes (RTECS , 2000) 34,500 mg/m(3) for 16W- intermittent -- Fatty liver degeneration; Changes in kidney, ureter, and Bladder; Effetc on amino acids (including renal excretion) (RTECS , 2000) 5000 ppm for 6H for 14W- intermittent -- Changes in circulation of brain and coverings (hemorrhage, thrombosis, etc.); Other changes in sense organs and special senses (Nose, Eye, Ear, and Taste); Death (RTECS , 2000) 500 ppm for 6H for 2Y- intermittent -- Other changes in sense organs and special senses (Nose, Eye, Ear, and Taste); Fibrosis, focal (pneumoconiosis) (RTECS , 2000)
TDLo- (ORAL)DOG: TDLo- (INTRAPERITONEAL)MOUSE: TDLo- (ORAL)RABBIT: TDLo- (IMPLANT)RAT: TDLo- (INTRAPERITONEAL)RAT: Female, 801 mg/kg at 5-15D of pregnancy -- Developmental abnormalities (RTECS , 2000) Female, 405 mg/kg at 5-15D of pregnancy -- Fetotoxicity (except death, e.g., stunted fetus) and other developmental (RTECS , 2000)
TDLo- (ORAL)RAT: 17,896 mg/kg for 35W- intermittent -- Ulceration or bleeding from stomach; Changes in Liver (RTECS , 2000) 10,500 mg/kg for 21D- intermittent -- Structural change in nerve or sheath; Somnolence (general depressed activity); Effects on lipids including transport (RTECS , 2000)
CALCULATIONS
1 ppm = 4.16 mg/m(3) (Verschueren, 1983) 1 mg/m(3) = 0.24 ppm (Verschueren, 1983)
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS80-62-6 (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 CAS80-62-6 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS80-62-6 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS80-62-6 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS80-62-6 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS80-62-6 (U.S. Environmental Protection Agency, 2010):
Listed as: Methyl methacrylate Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: 2-Propenoic acid, 2-methyl-, methyl ester Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS80-62-6 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS80-62-6 (U.S. Environmental Protection Agency, 2010b):
Listed as: Methyl methacrylate P or U series number: U162 Footnote: Listed as: 2-Propenoic acid, 2-methyl-, methyl ester P or U series number: U162 Footnote: Editor's Note: The D, F, and K series waste numbers and Appendix VIII to Part 261 -- Hazardous Constituents were not included. Please refer to 40 CFR Part 261.
- EPA SARA Title III, Extremely Hazardous Substance List for CAS80-62-6 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS80-62-6 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Methyl methacrylate Effective Date for Reporting Under 40 CFR 372.30: 1/1/87 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS80-62-6 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS80-62-6 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1247 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1247 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS80-62-6 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
Methyl methacrylate is moderately toxic by inhalation, mildly toxic by ingestion, and a skin and eye irritant. Avoid breathing vapors; keep upwind. Wear appropriate protective clothing and provide adequate ventilation to prevent exposure when working with or around methyl methacrylate (AAR, 1998; (ITI, 1995; Lewis, 1996; Sittig, 1991). It is a very dangerous fire and polymerization hazard when exposed to heat, light, oxygen, or ionizing radiation. Wash contaminated skin immediately; remove contaminated clothing immediately to prevent fire hazard (ITI, 1995; Lewis, 1996; Sittig, 1991).
HANDLING
- Personnel working with or around methyl methacrylate should have adequate ventilation in the area and wear appropriate protective clothing (ITI, 1995; Lewis, 1996; Sittig, 1991).
STORAGE
Store methyl methacrylate in tightly closed containers away from sources of polymerization hazard such as light, heat, oxygen, and ionizing radiation. Do not allow containers to become damaged (ITI, 1995; Sittig, 1991).
- ROOM/CABINET RECOMMENDATIONS
Store containers of properly inhibited methyl methacrylate in cool, well-ventilated areas. The preferred area is an isolated, outdoor storage area, but indoor storage is acceptable if stored in a combustible liquid storage room (ITI, 1995; Sittig, 1991).
Methyl methacrylate is incompatible with light, heat, caustics, nitrates, strong acids, aliphatic amines, alkanolamines, peroxides, and strong oxidizers (ITI, 1995; Pohanish & Greene, 1997; Sittig, 1991).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- Methyl methacrylate is moderately toxic by inhalation, mildly toxic by ingestion, and a skin and eye irritant. Avoid breathing vapors; keep upwind. Wear appropriate protective clothing and provide adequate ventilation to prevent exposure when working with or around methyl methacrylate (AAR, 1998; (ITI, 1995; Lewis, 1996; Sittig, 1991).
- It is a very dangerous fire and polymerization hazard when exposed to heat, light, oxygen, or ionizing radiation. Wash contaminated skin immediately; remove contaminated clothing immediately to prevent fire hazard (ITI, 1995; Lewis, 1996; Sittig, 1991).
EYE/FACE PROTECTION
- Wear appropriate eye protection to avoid eye injury from liquid splashes or vapor exposure (AAR, 1998; (Sittig, 1991).
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 80-62-6.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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.
Methyl methacrylate is a dangerous fire hazard and an explosive polymerization hazard when exposed to heat, flame, light, oxygen, or ionizing radiation (AAR, 1998; (ITI, 1995; Lewis, 1996; Lewis, 1997) NFPA, 1994; (Sittig, 1991). If methyl methacrylate is on fire or involved in a fire, do not attempt to extinguish the fire unless the flow of methyl methacrylate can be stopped. Cool affected containers with flooding quantities of water; containers may explode. Use flooding quantities of water as fog; solid streams of water may spread the fire. Apply water from as far away as possible or from a protected location. Use foam, dry chemical, or carbon dioxide to extinguish the fire (AAR, 1998; (Sittig, 1991).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS80-62-6 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Dry chemical, CO2, water spray or alcohol-resistant foam. Do not use dry chemical extinguishers to control fires involving nitromethane or nitroethane.
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
Water spray, fog or alcohol-resistant 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 129 (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 CAS80-62-6 (NFPA, 2002):
Acrid smoke and irritating fumes are emitted when methyl methacrylate is heated to decomposition (Lewis, 1996). Fires involving methyl methacrylate may release toxic gases and vapors, such as carbon monoxide (HSDB , 2000).
EXPLOSION HAZARD
- Methyl methacrylate is a dangerous fire hazard and an explosive polymerization hazard when exposed to heat, flame, light, oxygen, or ionizing radiation (AAR, 1998; (ITI, 1995; Lewis, 1996; Lewis, 1997) NFPA, 1994; (Sittig, 1991).
DUST/VAPOR HAZARD
- Methyl methacrylate vapor is a dangerous fire hazard when exposed to heat or flame. The vapors are heavier than air and may travel along the ground and flash back (AAR, 1998; (ITI, 1995; Lewis, 1996; Lewis, 1997) NFPA, 1994; (Sittig, 1991).
- The vapors are also a skin and eye irritant. Wear appropriate protective clothing and provide adequate ventilation (AAR, 1998; (ITI, 1995; Lewis, 1996; Sittig, 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).
- Based on its low flash point (10 degrees C; 50 degrees F), methyl methacrylate forms explosive mixtures with air and may form a heat-sensitive explosive product. Methyl methacrylate may also explode at its evaporation point of 60 degrees C (Lewis, 1996; Pohanish & Greene, 1997; Urben, 1995).
- It is incompatible with caustics, nitrates, strong acids (such as nitric acid, hydrochloric acid, and sulfuric acid), aliphatic amines, alkanolamines, peroxides, strong oxidizers (such as permanganates, perchlorates, and chlorates), and strong alkalis (such as sodium hydroxide and potassium hydroxide) (Pohanish & Greene, 1997; Sittig, 1991).
- Polymerization may occur due to heat, contamination, and/or the lack of appropriate inhibitor; spontaneous, explosive polymerization may cause containers to rupture violently (AAR, 1998; (Lewis, 1996; Pohanish & Greene, 1997; Urben, 1995).
Methyl methacrylate may polymerize violently when in contact with azoisobutyronitrile; dibenzyl peroxide, di-tert-butyl peroxide, or propionaldehyde (Lewis, 1996; Urben, 1995).
- Methyl methacrylate may be ignited by accumulated static electrical charges (Pohanish & Greene, 1997).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- LARGE SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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 129 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area for at least 50 meters (150 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate closed spaces before entering.
- If a fire involving methyl methacrylate becomes uncontrollable or its containers are exposed to direct flame, consider evacuating the area in a one-half (1/2) mile radius (AAR, 1998).
- If spilled or leaking methyl methacrylate is not on fire, consider evacuating the downwind area based on the amount of spilled methyl methacrylate, the location of the spill, and the weather conditions (AAR, 1998).
- AIHA ERPG Values for CAS80-62-6 (AIHA, 2006):
- DOE TEEL Values for CAS80-62-6 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Methyl methacrylate TEEL-0 (units = ppm): 17 TEEL-1 (units = ppm): 17 TEEL-2 (units = ppm): 120 TEEL-3 (units = ppm): 570 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 CAS80-62-6 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; United States Environmental Protection Agency Office of Pollution Prevention and Toxics, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS80-62-6 (National Institute for Occupational Safety and Health, 2007):
IDLH: 1000 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 129 (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 129 (ERG, 2004) If methyl methacrylate is not on fire and not involved in a fire, keep sparks, flames, and other sources of ignition away from the area. Restrict access to personnel wearing appropriate protective clothing and ventilate the area. Keep spilled methyl methacrylate out of water sources and sewers. Build dikes to contain the spill as necessary. Attempt to stop the leak only if this can be done without excessive risk to personnel. Absorb spill in vermiculite, dry sand, earth, or a similar material and place into sealed containers. Use water spray to knock down vapors (AAR, 1998; (Sittig, 1991). If methyl methacrylate is spilled on land, dig a pit, pond, lagoon or other holding area to contain the spilled liquid. Dike surface flow of spill using soil, sand bags, foamed polyurethane, or foamed concrete. Keep spill out of confined spaces such as sewers to avoid explosion hazard. Apply appropriate foam to diminish vapor and fire hazard. Apply "universal" gelling agent to immobilize the spill. Absorb contained liquid with fly ash, cement powder, or commercial sorbents (AAR, 1998; (Sittig, 1991). If methyl methacrylate is spilled onto water, use natural barriers or oil spill control booms to limit the spill travel. If approved by EPA, use a surface active agent (such as detergent, soaps, or alcohols). Inject a "universal" gelling agent to solidify the encircled spill and increase the effectiveness of the booms. If dissolved to a concentration of approximately 10 ppm or greater, apply activated carbon at ten times the amount spilled. Remove trapped methyl methacrylate with suction hoses and use mechanical dredges or lifts to remove the immobilized masses of pollutants and precipitates (AAR, 1998). If methyl methacrylate is spilled into the air, apply water spray or mist to knock down the vapors (AAR, 1998).
Incineration is a suggested disposal method. Mix methyl methacrylate with a more flammable solvent and spray the mixture into a furnace (ITI, 1995; Sittig, 1991). A fluidized-bed thermal oxidation system located in Franklin, Ohio, having a 7.6 m (25 ft) diameter secondary reaction chamber, burned an aqueous solution of methyl methacrylate monomer. The destruction and removal efficiency for the waste constituents was greater than 99.999% with temperatures of 788 to 843 degrees C (1450 to 1550 degrees F) for methyl methacrylate, with a residence time of approximately 11 seconds (Freeman, 1989).
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
- Methyl methacrylate is primarily released into the environment during its production and use in manufacturing. Spills and emissions of vapors may also occur during transport and storage. It does not have a known, natural source (Howard, 1989).
ENVIRONMENTAL FATE AND KINETICS
SURFACE WATER If released into water, methyl methacrylate will primarily be removed by volatilization. Hydrolysis may occur, but it is not a significant removal process. Removal through the reaction with photolytically produced hydroxyl radicals and through adsorption to sediments or particulates are also probably not important processes (Howard, 1989). The reported half life of methyl methacrylate in ground water ranges from 2 weeks (336 hours) to 8 weeks (1344 hours), based on the estimated aqueous unacclimated aerobic biodegradation rate (Howard et al, 1991). The reported half life of methyl methacrylate in surface water ranges from 7 days (168 hours) to 4 weeks (672 hours), based on the estimated aqueous unacclimated aerobic biodegradation rate (Howard et al, 1991).
TERRESTRIAL If released onto soil, methyl methacrylate will primarily be removed by volatilization and by leaching into ground waters. If the soil contains acclimated microorganisms, some biodegradation may occur (Howard, 1989). The reported half life of methyl methacrylate in the soil ranges from 7 days (168 hours) to 4 weeks (672 hours), based on the estimated aqueous unacclimated aerobic biodegradation rate (Howard et al, 1991).
ABIOTIC DEGRADATION
- Methyl methacrylate and nitrogen oxides in concentrations typical of urban areas underwent photodegradation with a half life of 2.7 hours; the half life increased to greater than 3 hours when the air concentrations reflected a typical rural mixture. Hydrolysis is a much less significant removal process with a reported half life of 3.9 years at pH 7, but 14 days at pH 9. Methyl methacrylate will probably not photolyze in the atmosphere, but may be able to react in natural waters due to the free radicals found there (Howard, 1989).
In air, the reported photooxidation half life ranges from 66 minutes (1.1 hours) to 9.7 hours, based on the estimated rate constants for vapor phase reactions with hydroxyl radicals and ozone in air (Howard et al, 1991). The reported first-order hydrolysis half life is 4 years based on the rate constant (kB = 200 M(-1)hr(-1)) at 25 degrees C and pH 7 (Howard et al, 1991). The reported base rate constant (M(OH-)-hr)(-1) is 200 M(-1)hr(-1) with t(1/2) = 14.4 days at pH 9. The rate constant was measured at 25 degrees C and pH 11 (Howard et al, 1991).
BIODEGRADATION
- Methyl methacrylate is reported to be significantly biodegraded in mixed inoculum of soil, surface water, and sewage, in activated sludge, and in a standard biodegradation test using sewage seed (Howard, 1989).
The reported aqueous aerobic half life of methyl methacrylate ranges from 7 days (168 hours) to 4 weeks (672 hours), based on unacclimated screening test data (Howard et al, 1991). The reported aqueous anaerobic half life of methyl methacrylate ranges from 4 weeks (672 hours) to 16 weeks (2688 hours), based on estimated unacclimated aerobic biodegradation (Howard et al, 1991).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- Ecotoxicity Values (HSDB , 2000):
Tlm - FATHEAD MINNOW (Pimephales promelas): 499-159 mg/L for 24-96H; Conditions of bioassay not specified Tlm - BLUEGILL (Lepomis macrochirus): 368-232 mg/L for 24-96H; Conditions of bioassay not specified Tlm - GOLDFISH (Carassius auratus): 423-277 mg/L for 24-96H; Conditions of bioassay not specified Tlm - GUPPIES (Lebistes reticulatus): 368 mg/L for 24-96H; Conditions of bioassay not specified Toxicity threshold (cell multiplication inhibition test) - BACTERIA (Pseudomonas putida): 100 mg/L Toxicity threshold (cell multiplication inhibition test) - ALGA (Microcystis aeruginosa): 120 mg/L Toxicity threshold (cell multiplication inhibition test) - GREEN ALGA (Scenedesmus quadricauda): 37 mg/L Toxicity threshold (cell multiplication inhibition test) - PROTOZOA (Entosiphon sulcatum): 450 mg/L Toxicity threshold (cell multiplication inhibition test) - PROTOZOA (Uronema parduczi Chatton-Lwoff): 556 mg/L
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Methyl methacrylate is a flammable, clear, colorless liquid; its odor has been described as distinctive, fruity, ester-like, acrid, and pungent. Methyl methacrylate monomer is a polymerization hazard when exposed to light, heat, oxygen, or ionizing radiation (AAR, 1998; ACGIH, 1999; (Ashford, 1994; Clayton & Clayton, 1994; ILO, 1998; Lewis, 1996; Lewis, 1997; Lewis, 1997; Verschueren, 1983).
PH
VAPOR PRESSURE
- 28 mmHg (at 20 degrees C) (Verschueren, 1983)
- 38.4 mmHg (at 25 degrees C) (Howard, 1989)
- 40 mmHg (at 25.5 or 26 degrees C) (ACGIH, 1999; (Clayton & Clayton, 1994; ILO, 1998; Lewis, 1996; Verschueren, 1983)
- 49 mmHg (at 30 degrees C) (Verschueren, 1983)
SPECIFIC GRAVITY
- NORMAL TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
DENSITY
FREEZING/MELTING POINT
-48 degrees C(Clayton & Clayton, 1994; Howard, 1989; ILO, 1998) -50 degrees C (Lewis, 1998; Verschueren, 1983)
BOILING POINT
- 100-101 degrees C (Ashford, 1994; Howard, 1989)
- 100 degrees C; 212 degrees F (NFPA, 1994)
- 100.5 degrees C (ILO, 1998)
- 101 degrees C (at 760 torr) (ACGIH, 1999; (Clayton & Clayton, 1994; Lewis, 1996; Lewis, 1997; Verschueren, 1983)
FLASH POINT
- 10 degrees C; 50 degrees F (open cup) (ACGIH, 1999; (Clayton & Clayton, 1994; ILO, 1998; Lewis, 1996; Lewis, 1997) NFPA, 1994)
- 13 degrees C(TOC) (Ashford, 1994)
AUTOIGNITION TEMPERATURE
- 421 degrees C; 790 degrees F (Lewis, 1997)
EXPLOSIVE LIMITS
1.7% (ILO, 1998) NFPA, 1994) 2.1% (ACGIH, 1999; (Clayton & Clayton, 1994; Lewis, 1996)
8.2% (ILO, 1998) NFPA, 1994) 12.5% (ACGIH, 1999; (Clayton & Clayton, 1994; Lewis, 1996)
SOLUBILITY
Methyl methacrylate is only slightly soluble in water (ACGIH, 1999; (Clayton & Clayton, 1994; ILO, 1998; Lewis, 1996; Lewis, 1997) NFPA, 1994): 15 g/L (at 20 degrees C) (Ashford, 1994) 15.6 g/L (at 20 degrees C) (Howard, 1989)
It is miscible in ethanol, diethyl ether, and acetone (ACGIH, 1999). Methyl methacrylate is very soluble in alcohol and ether and soluble in most organic solvents (Clayton & Clayton, 1994; Lewis, 1997).
OCTANOL/WATER PARTITION COEFFICIENT
- log KOW = 1.38 (Howard, 1989)
HENRY'S CONSTANT
- 3.11 X 10(-4) atm-m(3)/mol (Ehrenfeld et al, 1986)
- 3.24 x 10(-4) atm-m(3)/mol (calculated) (Howard, 1989)
SPECTRAL CONSTANTS
OTHER/PHYSICAL
294 degrees C (HSDB , 2000) 561 degrees F (HSDB , 2000) 567 K (HSDB , 2000)
-11,400 btu/lb (HSDB , 2000) 6310 cal/g (HSDB , 2000) -264 x 10(5) J/kg (estimated) (HSDB , 2000)
-248 btu/lb (HSDB , 2000) -138 cal/g (HSDB , 2000) -5.78 x 10(5) J/kg (HSDB , 2000)
- LIQUID WATER INTERFACIAL TENSION
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