CATECHOL
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures.
SYNONYM REFERENCE
- (RTECS , 1996; HSDB , 1996; OHM/TADS , 1996)
USES/FORMS/SOURCES
Catechol is commonly used as an antioxidant in the rubber, chemical, photographic, dye, fat, and oil industries. It is used in the manufacture of monomer inhibitors to stop radical polymerization, particularly the synthesis of the styrene polymerization inhibitor 4-t-butylcatechol (Clayton & Clayton, 1994) Hathaway, 1991; (HSDB , 1996). It also is used in fur dyeing, as a photographic developer, in electroplating, in light stabilizers, and in perfumes and specialty inks. It is used as a reagent in organic synthesis (Budavari, 1989) Hathaway, 1991; (Lewis, 1993). Medicinally, catechol is used as an antiseptic. It is also used in pharmaceutical formulations (Lewis, 1993) Hathaway, 1991). Catechol was formerly used as an anti-fungal preservative for treating seed potato pieces. It has also been used as a postharvest aid (HSDB , 1996).
SYNONYM EXPLANATION
- Many references use PYROCATECHOL as the primary chemical name for CAS 120-80-9.
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Catechol is a CNS depressant and an irritant of the eyes, skin, and mucous membranes.
- Symptoms of exposure may include seizures, increased blood pressure, blood dyscrasias, degenerative changes in the renal tubules, lacrimation or burns of the eyes, a burning sensation in the throat and lungs, cough, and eczematous dermatitis.
- Methemoglobinemia, leukopenia, and anemia have been reported in experimental animals following repeated exposure.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (ERG, 2004)
TOXIC; inhalation, ingestion, or skin contact with material may cause severe injury or death. Fire will 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 134 (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 EYE EXPOSURE - Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Contact lenses should not be worn when working with this chemical. DERMAL EXPOSURE - Immediately wash the contaminated skin with water. If this chemical penetrates the clothing, immediately remove the clothing and wash the skin with water. If symptoms occur after washing, get medical attention immediately. 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, respiratory system, CNS, and kidneys (National Institute for Occupational Safety and Health, 2007).
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.
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. 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.
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.
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 gastrointestinal tract irritation, CNS depression, or seizures, do not induce emesis. Significant esophageal or gastrointestinal tract irritation or burns may occur following ingestion. The possible benefit of early removal of some ingested material by cautious gastric lavage must be weighed against potential complications of bleeding or perforation. PREHOSPITAL ACTIVATED CHARCOAL ADMINISTRATION Consider prehospital administration of activated charcoal as an aqueous slurry in patients with a potentially toxic ingestion who are awake and able to protect their airway. Activated charcoal is most effective when administered within one hour of ingestion. Administration in the prehospital setting has the potential to significantly decrease the time from toxin ingestion to activated charcoal administration, although it has not been shown to affect outcome (Alaspaa et al, 2005; Thakore & Murphy, 2002; Spiller & Rogers, 2002). In patients who are at risk for the abrupt onset of seizures or mental status depression, activated charcoal should not be administered in the prehospital setting, due to the risk of aspiration in the event of spontaneous emesis. The addition of flavoring agents (cola drinks, chocolate milk, cherry syrup) to activated charcoal improves the palatability for children and may facilitate successful administration (Guenther Skokan et al, 2001; Dagnone et al, 2002).
ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old. 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.
Observe patients with ingestion carefully for the possible development of esophageal or gastrointestinal tract irritation or burns. If signs or symptoms of esophageal irritation or burns are present, consider endoscopy to determine the extent of injury.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
Approximate lethal oral doses of catechol are 0.3 g/kg for dogs; 0.2 g/kg for rabbits; 0.1 g/kg for cats; and 0.16 g/kg for guinea pigs. One subcutaneous injection of about 0.22 g/kg usually causes death in rats and guinea pigs. The lethal intravenous dose for dogs is approximately 0.04 g/kg (Clayton & Clayton, 1994).
MAXIMUM TOLERATED EXPOSURE
OCCUPATIONAL Japanese factory workers exposed to concentrations of catechol ranging from 8 mg/m(3) to 322 mg/m(3) over two years complained of cough with sputum production, occasional sore throat, some skin eruptions, and eye irritation. These workers were also exposed to phenol (Hathaway, 1991).
Rats exposed to catechol concentrations of 1500, 2000, or 2800 mg/m(3) for 8 hours lived. However, tremors appeared after 6 to 7 hours of exposure to 2000 and 2800 mg/m(3), and the effects persisted through the day following exposure (Hathaway, 1991). Post-exposure effects seen 14 days after exposure included blackened or missing toes, blackened tails, and missing tips of the tails of all animals exposed to 2800 mg/m(3) and in two of six rats exposed to 2000 mg/m(3). No toxic effects were observed in the group exposed to 1500 mg/m(3) (Hathaway, 1991).
- Carcinogenicity Ratings for CAS120-80-9 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Catechol A3 :Confirmed Animal Carcinogen with Unknown Relevance to Humans: The agent is carcinogenic in experimental animals at a relatively high dose, by route(s) of administration, at site(s), of histologic type(s), or by mechanism(s) that may not be relevant to worker exposure. Available epidemiologic studies do not confirm an increased risk of cancer in exposed humans. Available evidence does not suggest that the agent is likely to cause cancer in humans except under uncommon or unlikely routes or levels of exposure.
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): 2B ; Listed as: Catechol 2B : The agent (mixture) is possibly carcinogenic to humans. The exposure circumstance entails exposures that are possibly carcinogenic to humans. This category is used for agents, mixtures and exposure circumstances for which there is limited evidence of carcinogenicity in humans and less than sufficient evidence of carcinogenicity in experimental animals. It may also be used when there is inadequate evidence of carcinogenicity in humans but there is sufficient evidence of carcinogenicity in experimental animals. In some instances, an agent, mixture or exposure circumstance for which there is inadequate evidence of carcinogenicity in humans but limited evidence of carcinogenicity in experimental animals together with supporting evidence from other relevant data may be placed in this group.
NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Catechol 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 CAS120-80-9 (U.S. Environmental Protection Agency, 2011):
CALCULATIONS
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS120-80-9 (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 CAS120-80-9 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS120-80-9 (National Institute for Occupational Safety and Health, 2007):
Listed as: Catechol REL: IDLH: Not Listed
- OSHA PEL Values for CAS120-80-9 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS120-80-9 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS120-80-9 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS120-80-9 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS120-80-9 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS120-80-9 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS120-80-9 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS120-80-9 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS120-80-9 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions (49 CFR 172.101, 2005):
- ICAO International Shipping Name (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS120-80-9 (NFPA, 2002):
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Catechol is incompatible with strong oxidizers and nitric acid (NIOSH , 1996). Catechol turns brown when exposed to air or light, especially in the presence of moisture. Aqueous solutions quickly turn brown (Lewis, 1993; Budavari, 1989).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (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 in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- Personnel should wear a respirator or self-contained breathing apparatus, rubber gloves, apron, boots, and a face shield ((CHRIS, 1996); OHM/TADS , 1996).
- Protective barrier creams should be used (HSDB , 1996).
- Catechol which contacts the skin must be washed off within 1 hour to reduce the course of dermatitis since catechol quickly fixes to skin proteins (HSDB , 1996).
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 120-80-9.
ENGINEERING CONTROLS
- Local exhaust ventilation should be used to reduce concentrations of catechol in workplace air. Ventilation controls should be installed as close as possible to the point of generation (HSDB , 1996).
-PHYSICAL HAZARDS
FIRE HAZARD
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures. POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (ERG, 2004) Flammable/combustible material. May be ignited by heat, sparks or flames. When heated, vapors may form explosive mixtures with air: indoors, outdoors and sewers explosion hazards. Contact with metals may evolve flammable hydrogen gas. Containers may explode when heated.
Catechol is combustible when exposed to heat or to flames (Lewis, 1996).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS120-80-9 (NFPA, 2002):
- INITIATING OR CONTRIBUTING PROPERTIES
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (ERG, 2004)
Water spray, fog or alcohol-resistant foam. Move containers from fire area if you can do it without risk. Use water spray or fog; do not use straight streams. Do not get water inside containers. Dike fire control water for later disposal; do not scatter the material.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (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.
- NFPA Extinguishing Methods for CAS120-80-9 (NFPA, 2002):
- Fires involving catechol should be fought with water, carbon dioxide, dry chemical, or alcohol foam, although water and foam may be ineffective (Lewis, 1996; (CHRIS, 1996)).
DUST/VAPOR HAZARD
- Irritation of the eyes, nose, and throat may result from inhaling catechol dusts or mists ((CHRIS, 1996)).
REACTIVITY HAZARD
- Catechol is volatile with steam (Budavari, 1989).
- A hypergolic reaction results from contact of catechol with concentrated nitric acid. The ignition delay is 1 millisecond (Bretherick, 1990).
- Catechol is incompatible with strong oxidizers and nitric acid (NIOSH , 1996).
- Catechol turns brown when exposed to air or light, especially in the presence of moisture. Aqueous solutions quickly turn brown (Lewis, 1993; Budavari, 1989).
- Acrid smoke and irritating fumes are produced when catechol is heated to decomposition (Lewis, 1996).
- It is highly reactive under many situations (OHM/TADS , 1996).
- Catechol reduces ammoniacal silver nitrate and Fehling's solution (HSDB , 1996).
- It forms a definite compound with boric acid (HSDB , 1996).
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 134 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (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 134 (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 25 meters (75 feet) in all directions. Stay upwind. Keep unauthorized personnel away. Keep out of low areas. Ventilate enclosed areas.
- AIHA ERPG Values for CAS120-80-9 (AIHA, 2006):
- DOE TEEL Values for CAS120-80-9 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS120-80-9 (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 CAS120-80-9 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (ERG, 2004) Fully encapsulating, vapor protective clothing should be worn for spills and leaks with no fire. ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). Stop leak if you can do it without risk. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Prevent entry into waterways, sewers, basements or confined areas. Use clean non-sparking tools to collect material and place it into loosely covered plastic containers for later disposal.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 134 (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 in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
Apply carbon or peat to spills in water (OHM/TADS , 1996).
Disposal of catechol waste may be accomplished by incineration after combining with another flammable material such as paper. It may also be dissolved in a flammable solvent before spraying into a combustion chamber (HSDB , 1996). 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
- Releases of catechol to the environment may be possible through its use in various manufacturing processes. It has also been found in coal conversion wastewaters, crude wood tar, drainage water from bituminous shale, coal-tar chemical production effluents, and in cigarette smoke (HSDB , 1996).
- Naturally occurring sources of catechol include plants such as onions and apples, and crude beet sugar. It is also found in the tannin layer of the Douglas pine and in the leaves and branches of oak and willow (HSDB , 1996).
ENVIRONMENTAL FATE AND KINETICS
Based on the estimated vapor pressure of 3 x 10(-2) mmHg at 20 degrees C, catechol is expected to exist primarily in the vapor phase in the atmosphere. It will react with photochemically produced hydroxyl radicals (estimated half-life 0.645 days). It may also react with nitrate radicals during the night with an estimated half-life of 15 minutes (HSDB , 1996).
SURFACE WATER Catechol released to water will exist in a partially dissociated state based on its pKa of 9.23 for the initial ionization. This indicates that its reactivity and transport may be affected by pH (HSDB , 1996). Biodegradation may be an important fate process in water (HSDB , 1996). Photolysis will not be important for the non-ionized form of catechol since this form does not absorb light above 300 nm in methanol solution. However, the ionized form may photolyze based on an absorption maximum at 313 nm in basic aqueous solution (HSDB , 1996). Catechol may be subject to indirect photooxidation by hydroxyl and peroxy radicals in sunlit waters. Half-lives for the reactions with hydroxyl and peroxy radicals are estimated to be 100 and 19.2 hours of sunlight, respectively (HSDB , 1996). It is not expected to adsorb to sediment, based on a reported Koc of 118. Volatilization and hydrolysis will not be important fate processes in water (HSDB , 1996).
TERRESTRIAL Catechol released to soil is likely to be highly mobile, due to the reported Koc of 118. Significant leaching to groundwater is possible; biodegradation may occur depending on the rate of leaching (HSDB , 1996). Catechol may exist in a partially dissociated state in moist soils due to its pKa of 9.23; its transport and reactivity may be affected by pH (HSDB , 1996). Volatilization from soil and hydrolysis are not expected to be important fate processes (HSDB , 1996).
BIODEGRADATION
- Biodegradation of catechol is expected to be an important removal process in water, based on activated sludge and sewage studies. It is moderately to readily biodegraded in soils (HSDB , 1996).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- The effects of low concentrations of catechol on aquatic organisms is not known ((CHRIS, 1996)).
- ECOTOXICITY VALUES (HSDB , 1996):
EC50, Pimephales promelas (fathead minnow), 9.00 mg/L/96H (confidence limit 8.47 to 9.65 mg/L), flow through bioassay with measured concentrations, temperature 25.6 degrees C, dissolved oxygen 6.4 mg/L, hardness 46.0 mg/L calcium carbonate, alkalinity 40.2 mg/L calcium carbonate, pH 7.7. Effect was loss of equilibrium. LC50, Pimephales promelas (fathead minnow), 9.22 mg/L/96H (confidence limit 8.62 to 9.87 mg/L), flow through bioassay with measured concentrations, temperature 25.6 degrees C, dissolved oxygen 6.4 mg/L, hardness 46.0 mg/L calcium carbonate, alkalinity 40.2 mg/L calcium carbonate, and pH of 7.7.
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Catechol is a colorless or white, crystalline solid with a faint, characteristic or phenolic odor and a sweet and bitter taste (ACGIH, 1991; HSDB , 1996; (CHRIS, 1996)).
Catechol turns brown when exposed to air or light, especially in the presence of moisture. Aqueous solutions quickly turn brown (Lewis, 1993; Budavari, 1989).
- It sublimes readily and appears as a vapor in air at ordinary temperatures. It also volatilizes with steam (ACGIH, 1991; Budavari, 1989).
PH
- Catechol is weakly acidic (OHM/TADS , 1996).
VAPOR PRESSURE
- 3 x 10(-2) mmHg (at 20 degrees C) (estimated) (HSDB , 1996)
- 10 mmHg (at 244 degrees F) (NIOSH , 1996)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
- TEMPERATURE AND/OR PRESSURE NOT LISTED
FREEZING/MELTING POINT
BOILING POINT
- 245.5 degrees C (at 760 mmHg) (Budavari, 1989)
- 221.5 degrees C (at 400 mmHg) (Budavari, 1989)
- 197.7 degrees C (at 200 mmHg) (Budavari, 1989)
- 176 degrees C (at 100 mmHg) (Budavari, 1989)
- 161.7 degrees C (at 60 mmHg) (Budavari, 1989)
- 150.6 degrees C (at 40 mmHg) (Budavari, 1989)
- 134 degrees C (at 20 mmHg) (Budavari, 1989)
- 118.3 degrees C (at 10 mmHg) (Budavari, 1989)
- 104 degrees C (at 5 mmHg) (Budavari, 1989)
FLASH POINT
- 127.2 degrees C; 261 degrees F (closed cup) (ACGIH, 1991; Lewis, 1996)
AUTOIGNITION TEMPERATURE
- 510 degrees C (HSDB , 1996)
EXPLOSIVE LIMITS
SOLUBILITY
Soluble in 2.3 parts water (Budavari, 1989) 44% by weight (NIOSH , 1996)
Catechol is soluble in chloroform and ether. It is very soluble in pyridine, acetone, and ethanol (Budavari, 1989; ACGIH, 1991). It is slightly soluble in cold benzene, and soluble in hot benzene, carbon tetrachloride, and acetate (HSDB , 1996).
OCTANOL/WATER PARTITION COEFFICIENT
- log Kow = 0.88 (measured) (HSDB , 1996)
HENRY'S CONSTANT
- 8.1 x 10(-11) (estimated) (HSDB , 1996)
OTHER/PHYSICAL
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