2-CHLOROPHENOL
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
IMO CLASSIFICATION:6.1 - Chlorophenol, liquid or solid STANDARD INDUSTRIAL TRADE CLASSIFICATION NUMBER:51244
SYNONYM REFERENCE
- (CHRIS , 2001; HSDB , 2001; NFPA, 1997; OHM/TADS, 2001; RTECS , 2001)
USES/FORMS/SOURCES
This compound is used in organic synthesis (dyes), as a chemical intermediate in the manufacture of dyestuff, higher chlorinated (un-isolated) phenols and preservatives (HSDB , 2001; Lewis, 1997a; Lewis, 1998). It is used to extract sulfur and nitrogen compounds from coal, and in the production of catechols (HSDB , 2001). It may be used as a chemical intermediate in the manufacture of phenolic resins and as a solvent for polyester fibers (HSDB , 2001). It finds use as a fire-retarded phenolic resin co-monomer (Ashford, 1994a). It is used in or is used as medications (HSDB , 2001). It is a component of disinfectants (HSDB , 2001). Due to its bacteriocidal (both gram-negative and gram-positive vegetative forms of animal pathogenic bacteria) and germicidal action, SEPTI-KLEEN is used to disinfect household and bathroom premises, sickroom premises and equipment, swimming pool related premises, garbage containers. PINE-O disinfectant is primarily used in bathroom premises (HSDB , 2001).
When used as a 1-5% emulsion, it can be used to kill within a few hours various Ascarid eggs and larvae on soil, brick, concrete, metal and wood surfaces (HSDB , 2001). It can be used as a soil sterilant (HSDB , 2001). It is used in the manufacture of the insecticide Profenofos (HSDB , 2001).
2-chlorophenol is a colorless to yellow-brown, or white to straw colored liquid (NFPA, 1997; Lewis, 1997a). Its odor has been described as: unpleasant and penetrating, heavy medicinal, phenolic, or carbolic (Ashford, 1994a; Lewis, 1997a; NFPA, 1997). In its pure state, this compound is colorless, whereas the technical grade may appear light tan or slightly pink due to impurities (OHM/TADS, 2001). Technical grade of chlorophenols may have impurities of chlorinated 2-phenoxyphenols, chlorinated diphenylethers, and chlorinated dibenzofurans (HSDB , 2001).
2-chlorophenol can be produced using the following methods: oxidation of o-chlorocumenes to peroxides, followed by hydration (HSDB , 2001); reaction of chlorine monoxide with phenol in carbon tetrachloride (yields 22% of 2-chlorophenol) (HSDB , 2001); chlorination of phenols (Lewis, 1997a); ring chlorination of phenol using sodium hypochlorite (Ashford, 1994a).
It is the generated during hydrolysis of hexachlorocyclohexane (OHM/TADS, 2001).
SYNONYM EXPLANATION
- The soluble concentrate SEPTI-KLEEN contains 10% isopropanol, 5% chlorophenol, 2% methyl salicylate and 6.5% soap (HSDB , 2001).
- The emulsifiable concentrate PINE-O DISINFECTANT contains 3.5% chlorophenol, 22% pine oil, and 7.5% soap (HSDB , 2001).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- 2-chlorophenol may be toxic from inhalation, ingestion, or dermal exposure and is irritating to the eyes, skin, and mucous membranes. Signs and symptoms of exposure may include pallor, sweating, hypotension, abdominal pain, vomiting, muscle weakness, tremor, and seizures. Pulmonary edema, methemoglobinemia, and Heinz body hemolytic anemia may develop. Damage to the liver, kidneys, spleen, and pancreas may occur.
- 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.
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. Carefully observe patients with inhalation exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
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. Some chemicals can produce systemic poisoning by absorption through intact skin. Carefully observe patients with dermal exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
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 and seizures, DO NOT induce emesis. Dilution may enhance absorption of 2-chlorophenol and should be avoided. 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.
HYPOTENSION: Infuse 10 to 20 mL/kg isotonic fluid. If hypotension persists, administer dopamine (5 to 20 mcg/kg/min) or norepinephrine (ADULT: begin infusion at 0.5 to 1 mcg/min; CHILD: begin infusion at 0.1 mcg/kg/min); titrate to desired response. 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
Oral exposure to 8 g or more results in rapid circulatory collapse and death (HSDB , 2001). Extrapolation from animal data suggests that the lethal dose for humans may be between one teaspoon and one ounce for a 150 pound adult (Sittig, 1991).
MAXIMUM TOLERATED EXPOSURE
The maximum tolerated human exposure to this agent has not been delineated. Chlorophenols have been classified by IARC as a group 2B carcinogen. Individual chlorophenols have not been classified ((ATSDR, 1999)). Exposure to 38,000 ppm caused skin tumors in rats (OHM/TADS, 2001).
- Carcinogenicity Ratings for CAS95-57-8 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed EPA (U.S. Environmental Protection Agency, 2011): Not Assessed under the IRIS program. ; Listed as: 2-Chlorophenol IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed MAK (DFG, 2002): Not Listed NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS95-57-8 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 5x10(-3) mg/kg-day
Inhalation: Drinking Water:
References: ATSDR, 1999 HSDB, 2001 IRIS, 2001; ITI, 1995 OHM/TADS, 2001 RTECS, 2001 LCLo- (INHALATION)RAT: LD50- (INTRAPERITONEAL)MOUSE: LD50- (ORAL)MOUSE: LD50- (SKIN)RABBIT: LD50- (INTRAPERITONEAL)RAT: LD50- (ORAL)RAT: 40 mg/kg -- Pulmonary emboli; Other changes in liver; Weight loss or decreased weight gain 670 mg/kg (OHM/TADS, 2001)
LD50- (SKIN)RAT: LD50- (SUBCUTANEOUS)RAT: LDLo- (SUBCUTANEOUS)GUINEA_PIG: LDLo- (INTRAVENOUS)RABBIT: LDLo- (SKIN)RABBIT: LDLo- (SUBCUTANEOUS)RABBIT: TDLo- (ORAL)MOUSE: TDLo- (SKIN)MOUSE: 4800 mg/kg for 12W - intermittent -- Equivocal tumorigenic agent by RTECS criteria; Tumors on skin and appendages 38 mg/kg for 12 W (ITI, 1995)
TDLo- (ORAL)RAT: Female, 4550 mg/kg; 70D prior to mating and 1-21D of pregnancy -- Effect on litter size (e.g., number fetuses per litter, measured before birth); Stillbirth
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS95-57-8 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS95-57-8 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS95-57-8 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS95-57-8 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS95-57-8 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS95-57-8 (U.S. Environmental Protection Agency, 2010):
Listed as: Phenol, 2-chloro- Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: 2-Chlorophenol Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: o-Chlorophenol Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS95-57-8 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS95-57-8 (U.S. Environmental Protection Agency, 2010b):
Listed as: o-Chlorophenol P or U series number: U048 Footnote: Listed as: Phenol, 2-chloro- P or U series number: U048 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 CAS95-57-8 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS95-57-8 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS95-57-8 (49 CFR 172.101 - App. B, 2005):
Listed as Chlorophenolates, liquid Severe Marine Pollutant: Yes Listed as Chlorophenolates, solid Severe Marine Pollutant: Yes
- EPA TSCA Inventory for CAS95-57-8 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2021 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2021 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS95-57-8 (NFPA, 2002):
-HANDLING AND STORAGE
HANDLING
- Personnel handling this compound should be trained in proper handling and storage procedures prior to working with it (Sittig, 1991).
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Store tightly closed containers in cool, dry, well-ventilated location (NFPA, 1997; Sittig, 1991).
Store separate from oxidizers and organic acids (NFPA, 1997). This compound attacks aluminum and copper. Exposure to air may lead to formation of explosive mixtures (Pohanish & Greene, 1997).
-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.
- Fire fighting personnel should wear butyl gloves, protective clothing, self-contained breathing apparatus and safety shoes (OHM/TADS, 2001).
- Always wear appropriate protective clothing and positive pressure self-contained breathing apparatus, especially when handling broken packages (AAR, 2000).
- Immediately remove contaminated clothing and isolate it at the site (AAR, 2000).
- Dispose of contaminated clothing items via incineration (ITI, 1995).
EYE/FACE PROTECTION
- When handling this liquid, splash-proof chemical goggles and face shield should be worn, unless full facepiece respiratory protection is used (Sittig, 1991).
- If material contacted the eyes skin, immediately flush for at least 15 minutes with running water (AAR, 2000).
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 95-57-8.
-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.
This compound is corrosive and combustible (Lewis, 1997; NFPA, 1997). The compound is flammable and presents a moderate fire hazard when exposed to heat, flames or oxidizers (Lewis, 2000; OHM/TADS, 2001). This compound may burn, but does not readily ignite (Sittig, 1991). Reaction with strong oxidizers may cause fire (Pohanish & Greene, 1997).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS95-57-8 (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 CAS95-57-8 (NFPA, 2002):
- Use alcohol foam (OHM/TADS, 2001).
- Suitable fire extinguishing materials are dry chemical, carbon dioxide, water spray, or foam extinguisher (Sittig, 1991).
- Combat small fires with dry chemical, carbon dioxide, water spray or foam. Large fires can be extinguished using water spray, fog or foam (CHRIS , 2001).
- Use extinguishing agent suitable for the type of surrounding fire. Prevent run-off water from leaking into sewers and water sources (AAR, 2000).
- Water spray can be used to keep containers cool in fire situations and to knock down vapors (NFPA, 1997).
- Approach fire from upwind. Do not inhale vapors and toxic decomposition compounds (NFPA, 1997).
When heated, poisonous chloride fumes are released (CHRIS , 2001). "Combustion may produce irritant and toxic gases" (NFPA, 1997). Heating to decomposition results in the release of toxic and corrosive fumes of hydrochloric acid and chlorine (ILO , 1998).
EXPLOSION HAZARD
- Containers with this chemical may explode when exposed to heat of a fire (CHRIS , 2001).
- This compound forms explosive mixtures with air. Reaction with strong oxidizers may result in explosion (Pohanish & Greene, 1997).
REACTIVITY HAZARD
- This compound reacts with oxidizing materials. During the reactions ethers, esters, or salts of metals and amines may be formed (OHM/TADS, 2001).
- This compound reacts with some oxidizers and with organic acids (NFPA, 1997).
- This compound reacts with air, oxidizers, aluminum and copper (Pohanish & Greene, 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 CAS95-57-8 (AIHA, 2006):
- DOE TEEL Values for CAS95-57-8 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS95-57-8 (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; 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National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS95-57-8 (National Institute for Occupational Safety and Health, 2007):
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.
In spill situations, all treatment procedures should be confirmed with the responsible environmental engineer and the regulatory official. In situ amelioration may consist of containment and isolation of the spill, and construction of clay/bentonite swales. Isolation procedures may include the construction of bentonite- or epoxy-lined dams, interceptor trenches, or impoundments. Treatment alternatives for contaminated water may include ultraviolet and solar oxidation, powdered activated carbon sorption, granular activated carbon filtration, biodegradation, bentonite or peat moss sorption (OHM/TADS, 2001). Take measures to prevent leakage into water intakes. Notify operators of nearby water intakes, local health and wildlife officials (CHRIS , 2001). Attempt to stop leak without putting emergency personnel at risk (AAR, 2000; (NFPA, 1997). Following a spill or leak, remove all ignition sources and ventilate the area (Sittig, 1991). Approach spill site from upwind. Avoid breathing vapors and do not allow the compound. to contact the skin (AAR, 2000). Absorb spilled compound in non-combustible material for later disposal (NFPA, 1997). Following a spill or leak, the liquid can be absorbed in vermiculite, dry sand, earth, or similar material and kept in sealed container for later disposal (Sittig, 1991). "Disposal of wastes containing chlorophenols is controlled by a number of federal regulations" ((ATSDR, 1999)). "The recommended method of disposing of large amounts of higher chlorinated phenols is incineration, preferably after mixing with another combustible fuel. Necessary precautions include the assurance of complete combustion in order to prevent the formation of toxic phosgene gas and the use of an acid scrubber to remove any halo-acids produced during combustion" ((ATSDR, 1999)).
"Disposal of wastes containing chlorophenols is controlled by a number of federal regulations" ((ATSDR, 1999)). "The recommended method of disposing of large amounts of higher chlorinated phenols is incineration, preferably after mixing with another combustible fuel. Necessary precautions include the assurance of complete combustion in order to prevent the formation of toxic phosgene gas and the use of an acid scrubber to remove any halo-acids produced during combustion" ((ATSDR, 1999)). Mix with combustible solvent (such as alcohol, benzene etc) and spray mixture into furnace with afterburner and scrubber (ITI, 1995; Sittig, 1991). Pour compound into sodium bicarbonate or a 9:1 mixture of sand and soda-ash, transfer into paper carton filled with packing paper. Burn in an open furnace, or in a furnace with afterburner and scrubber (ITI, 1995). Experiments on the feasibility of using ozonation to destroy 2-chlorophenol in wastewater showed that under acidic conditions, mainly the following four carboxylic acids are generated: tartaric acid, oxalic acid, maleic acid and hydroxymaleic acid (Jung, 2001). 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
- 2-chlorophenol is a synthetic organic compound and is not known to occur naturally. It is released to the environment from its use in the manufacture of synthetic chemicals, primarily dyes and higher chlorinated phenols (Howard, 1989).
- Exposure to 2- chlorphenol is possible following ingestion of chlorine-treated drinking water, or occupationally in workers of the synthetic chemical industry (Howard, 1989).
- Microbiological degradation of the herbicides 2,4-D and 2,4,5-T and the pesticides Silvex, Ronnel, lindane and benzene hexachloride, results in formation of various chlorophenols as metabolic intermediates (HSDB, 2004).
ENVIRONMENTAL FATE AND KINETICS
Following release to the atmosphere, 2-chlorophenol may undergo photolysis or reaction with nitric oxide (NO). Removal from the air may occur through washout (Howard, 1989). The estimated vapor phase half-life in atmosphere is 1.96 days (Howard, 1989).
SURFACE WATER Volatilization and sorption play only minor roles in the removal of 2-chlorophenol (OHM/TADS, 2001). The probable aquatic fate process for 2-chlorophenol is unknown. The anion of 2-chlorophenol can be expected to undergo photolysis in surface waters, but the resulting products are unknown. Due to the presence of a highly resistant covalent bond between the aromatic ring and the hydroxyl substituent, hydrolysis is not expected to be a significant process in water (OHM/TADS, 2001). Due to its moderate vapor pressure, volatilization of this compound may take place from surface waters. At low concentrations, this process is counteracted by 2-chlorophenol's relatively good solubility in water (OHM/TADS, 2001). The dissociation constant of 8.52 indicates that in water and moist soils, this compound exists in a partially dissociated state, which should have an impact on its transport and reactivity (Howard, 1989). Absorption to sediment occurs (Howard, 1989). When this compound was irradiated at 296 nm in aqueous solution at pH 8-13, photolysis generated mainly pyrocatechol from the undissociated form of 2-chlorophenol and mainly cyclopentadienic acid from its dissociated form (Howard, 1989). The half-life for evaporation from water 23.8 degrees C was 1.35 hours in stirred, static water 0.38 cm deep. Using Henry's Law constant of 5.6X10(-7) atm-m(3)/mole, the estimated half-life was 73 days for evaporation from a model river 1 m deep, flowing at 1 m/sec with a wind velocity of 3 m/sec (Howard, 1989).
GROUND WATER
TERRESTRIAL This compound exists mainly in a partially dissociated state. Adsorption to the soil is expected to be low to moderate based on estimated Koc-values ranging from 16 to 352(Howard, 1989). The decomposition rate for complete disappearance of this compound is 14 days in soil suspension, and 64 days by soil microflora (OHM/TADS, 2001). The half-life for evaporation from soil at 23.8 degrees C was 1.60 hours (Howard, 1989).
OTHER The suggested half-lives of 2-chlorophenol are (HSDB, 2004):
ABIOTIC DEGRADATION
- In the atmosphere, 2-chlorophenol may be degraded by photolysis or reaction with nitric oxide (NO). The vapor phase half-life is short, at less than two days. Airborne concentrations may also be removed by wet deposition. It may undergo photolysis in surface waters. Hydrolysis is not significant. Volatilization and sorption are also not important fate mechanisms. The dissociation constant indicates that 2-chlorophenol will exist in a partially dissociated state in water and moist soils. Low to moderate adsorption in soil occurs based on estimated organic carbon partition coefficients (Kocs). As a result, it may leach to groundwater. Biodegradation in soil is anticipated to be an important process (Howard, 1989; OHM/TADS, 2001).
BIODEGRADATION
- Biodegradation is expected to be an important process; 94% of 2-chlorophenol was lost within 6.5 hours when non-sterile soil was incubated with it at 4 degrees C. One percent was lost within 12 days, when sterile soil was used (Howard, 1989).
- Microbial degradation and photolysis are the two most important processes in aquatic sewage (OHM/TADS, 2001).
- Provided that oxygen is not limited, a degradative microflora able to rapidly degrade 2-chlorphenol may be established and maintained in stagnant, receiving waters with stable high levels of 2-chlorphenol. Biodegradation is significantly slower in fast-flowing receiving waters (OHM/TADS, 2001).
- 2-chlorophenol disappeared completely within 3-9 days with microbial decomposition (OHM/TADS, 2001).
- The decomposition rate for complete disappearance of this compound is 64 days by soil microflora (OHM/TADS, 2001).
- Removal via biodegradation was seen within 13 and 36 days in die-away tests using two raw river waters, within 15 days in two river waters seeded from the previous die-away test, and within 15 days in acclimated river water (Howard, 1989).
- Results from assays of biodegradation of 2-chlorophenol in a continuous-flow fluidized-bed aerobic reactor showed that Alcaligenes sp. bacteria grew exponentially within 48 hours when the initial inoculum contained at least 10(5) cells/mL. At a cell density of 10(5), but not at 10(6), a lag period was observed. When the culture medium was kept at pH 5, biodegradation of 2-chlorophenol was delayed. The removal of 2-chlorophenol was greater than 97% (Gallego et al., 2001).
BIOACCUMULATION
Bioconcentration is not expected to occur (Howard, 1989). Based on this compound's log Kow of 8.52 and its water solubility, a bioconcentration factor between 1.9 and 25 has been calculated (Howard, 1989). Bioconcentration factors: Bluegill sunfish: 214 (Howard, 1989) Goldfish: 7.1 (Howard, 1989) Goldfish: 6 (HSDB, 2004) Carp: 14-29 (HSDB, 2004)
ENVIRONMENTAL TOXICITY
- At very low concentrations, 2-chlorophenol may be toxic to aquatic life(CHRIS , 2001).
- Using standardized testing procedures for acute oral toxicity, redwinged blackbirds were found to be the most sensitive of 68 wild and domestic animals tested (HSDB, 2004).
EC50 - (WATER) ALGAE (Chlorella pyrenoidosa): 500,000 mcg/L -- complete destruction of chlorophyll (HSDB, 2004) LC50 - (WATER) CLADOCERAN (Daphnia magna): 2580 mcg/L for 96H; conditions of bioassay not specified (HSDB, 2004) LC50 - (WATER) GOLDFISH (Carassius auratus): 12,370 mcg/L for 96H; static, unmeasured bioassay (HSDB, 2004) LC50 - (WATER) FATHEAD MINNOW (Pimephales promelas): 11,630 mcg/L for 96H; static, unmeasured bioassay (HSDB, 2004) LC50 - (WATER) GUPPY (Poecilia reticulata): 20,170 mcg/L for 96H; static, unmeasured bioassay (HSDB, 2004) LC50 - (WATER) BLUEGILL (Lepomis machrochirus): 6590 mcg/L for 96H; static, unmeasured bioassay (HSDB, 2004) LDLo - (subQ) FROG: 400 mg/kg (RTECS, 2001) LD50 - (ORAL) REDWING BLACKBIRD: >113 mg/kg (HSDB, 2004) TLm - (WATER) BLUEGILL, Fingerlings: 8.4 ppm for 96H; cold water (CHRIS, 2001; OHM/TADS, 2001) TLm - (WATER) BLUEGILL SUNFISH: 8.2 ppm for 24H; warm water (CHRIS, 2001; OHM/TADS, 2001) TLm - (WATER) BLUEGILL: 12-8 ppm for 24-96H (OHM/TADS, 2001) TLm - (WATER) FATHEADS: 22-11 for 24-96H (OHM/TADS, 2001) TLm - (WATER) GOLDFISH: 15-12 ppm for 24-96H (OHM/TADS, 2001) TLm - (WATER) GUPPIES: 23-20 ppm for 24-96H (OHM/TADS, 2001)
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- 2-chlorophenol is a colorless to yellow-brown, or white to straw colored liquid (Lewis, 1997; NFPA, 1997).
- Its odor has been described as: unpleasant and penetrating, heavy medicinal, phenolic, or carbolic (Ashford, 1994; Lewis, 1997; NFPA, 1997).
- Colorless to yellow-brown crystals (ITI, 1995).
PH
- Weakly acidic (HSDB , 2001)
VAPOR PRESSURE
- 1.0 mmHg (at 12.1 degrees C) (Lewis, 2000; OHM/TADS, 2001)
- 2.2 mmHg (at 20 degrees C) (OHM/TADS, 2001)
- 0.99 mmHg (at 25 degrees C) ((ATSDR, 1999))
- 1.42 mmHg (at 25 degrees C) (Howard, 1989)
- 2.53 mmHg (at 25 degrees C) (HSDB , 2001)
- 40 mmHg (at 82 degrees C) (OHM/TADS, 2001)
- 100 mmHg (at 106 degrees C) (OHM/TADS, 2001)
SPECIFIC GRAVITY
- NORMAL TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
1.263 (at 20/4 degrees C) (Lewis, 2000) 1.2634 (at 20/4 degrees C) ((ATSDR, 1999); HSDB , 2001)
- TEMPERATURE AND/OR PRESSURE NOT LISTED
DENSITY
- NORMAL TEMPERATURE AND PRESSURE
- OTHER TEMPERATURE AND/OR PRESSURE
1.265 g/mL (at 15.5 degrees C) (ITI, 1995; Lewis, 1997; OHM/TADS, 2001) 1.27 kg/L (at 20 degrees C) (Ashford, 1994)
FREEZING/MELTING POINT
9.3 degrees C (Lewis, 1997) 9.3 degrees C; 48.7 degrees F; 282.5 K (CHRIS , 2001) 8 degrees C (Ashford, 1994) 7 degrees C (Lewis, 2000) 9.8 degrees C (HSDB , 2001)
7-9.3 degrees C (OHM/TADS, 2001) 9.3 degrees C ((ATSDR, 1999); Howard, 1989; ITI, 1995; ILO , 1998) 9 degrees C (Lewis, 2000) 9 degrees C; 49 degrees F (NFPA, 1997)
BOILING POINT
- 175 degrees C (Ashford, 1994; ILO , 1998; ITI, 1995; Lewis, 1997; OHM/TADS, 2001)
- 175 degrees C; 347 degrees F (NFPA, 1997)
- 174.5 degrees C; 346.1 degrees F; 447.7 K (CHRIS , 2001)
- 174.9 (at 760 mmHg) ((ATSDR, 1999); Howard, 1989; HSDB , 2001; Lewis, 2000)
FLASH POINT
- 107 degrees C; 225 degrees F (Lewis, 1997)
- 64 degrees C; 147 degrees F (NFPA, 1997)
- 93 degrees C (Pensky-Martens closed cup) (Ashford, 1994)
- 64 degrees C (closed cup) ((ATSDR, 1999); ILO , 1998)
- 147 degrees F (closed cup) (CHRIS , 2001; Lewis, 2000)
- 225 degrees F (AAR, 2000)
EXPLOSIVE LIMITS
SOLUBILITY
Very soluble in water (AAR, 2000; (Lewis, 1997) Sparingly or slightly soluble in water (Ashford, 1994; ILO , 1998; ITI, 1995; Lewis, 2000; OHM/TADS, 2001) Not soluble in water (NFPA, 1997) 2850 ppm (at 20 degrees C) (OHM/TADS, 2001) 28,000 ppm (at 25 degrees C) (Howard, 1989) 20,000 ppm (at 25 degrees C) ((ATSDR, 1999)) 11,400 mg/L (at 25 degrees C) (HSDB , 2001)
Soluble in alcohol (e.g. ethanol) and ether (e.g. ethyl ether) (HSDB , 2001; ITI, 1995; Lewis, 1997; Lewis, 2000). Soluble in oxygenated and aromatic solvents (e.g. benzene, acetone) (Ashford, 1994; (ATSDR, 1999); HSDB , 2001).
Soluble in aqueous alkali, such as sodium hydroxide (Ashford, 1994; (ATSDR, 1999); ITI, 1995; Lewis, 1997; Lewis, 2000)
OCTANOL/WATER PARTITION COEFFICIENT
- Log Kow = 2.17 ((ATSDR, 1999); OHM/TADS, 2001)
- Log Kow = 2.15 (Howard, 1989; HSDB , 2001)
HENRY'S CONSTANT
- 5.6X10(-7) atm-m(3)/mole (Howard, 1989)
- 6.8X10(-6) atm-m(3)/mole ((ATSDR, 1999))
SPECTRAL CONSTANTS
OTHER/PHYSICAL
- NUCLEAR MAGNETIC RESONANCE
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