CYCLOHEXANONE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
CYCLOHEXANONE ANONE CICLOESANONE (Italian) CYCLOHEXANON (Dutch) CYCLOHEXYL KETONE CYKLOHEKSANON (Polish) HEXANON HYTROL O KETOHEXAMETHYLENE NADONE PIMELIC KETONE PIMELIN KETONE SEXTONE
IDENTIFIERS
USES/FORMS/SOURCES
It is used as a solvent (ACGIH, 1986; Massoud et al, 1980) and is also a deliberately abused solvent (Crooke, 1972).
CYCLOHEXANONE is a white to pale yellow, oily liquid with an odor similar to those of peppermint and acetone (Sax, 1984; HSDB). It is somewhat soluble in water (87 g/L at 68 degrees F/20 degrees C), and is soluble in acetone, alcohol, ether, and organic solvents (HSDB).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Inhalation or contact with material may irritate or burn skin and eyes. Fire may produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control may cause pollution.
ACUTE CLINICAL EFFECTS
- Cyclohexanone is an eye, nose, and throat irritant at an airborne concentration of 50 ppm; 75 ppm causes marked irritation; and 125 ppm causes significant irritation (Clayton & Clayton, 1982). Occasional skin contact may not cause irritation; however, cyclohexanone can be absorbed through intact skin (HSDB). Inhalation of the vapors or mist can cause CNS depression (HSDB), with nausea, headache, weakness, dizziness, and loss of coordination.
- Skin uptake of liquid cyclohexanone was of minor importance in 3 human volunteers; measured absorption rates were 0.037 to 0.069 mg/cm(2)/hour (Mraz et al, 1994).
- Cyclohexanone caused skin irritation in rabbits and corneal damage in rats and rabbits with direct exposure (HSDB, Anon, 1967).
CHRONIC CLINICAL EFFECTS
- No serious industrial cyclohexanone poisonings have been reported (HSDB). It can have a defatting effect on the skin (HSDB). Cyclohexanone has caused damage to the liver and kidneys in rabbits exposed by inhalation to an airborne concentration of 190 ppm (ACGIH, 1986), and degenerative damage in many organs and anemia in the guinea pig with injection exposure (Ceresa & Grazioli, 1951). It caused CNS depression, respiratory failure, and general vascular and tissue reactions in experimental animals (Gupta, 1979).
- Cyclohexanone did not cause damage to the peripheral nervous system in rats, in contrast to n-hexane (Perbellini, 1981). Chronic intoxication stimulated CNS activity for up to 1.5 months in rats, then inhibited it for 2 to 3 months, followed by normalization after 4 to 5 months of administration (Pavlenko & Guseva, 1973).
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. Wash skin with soap and water. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. Keep victim warm and quiet. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
INHALATION EXPOSURE - INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm.
DERMAL EXPOSURE - 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). 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).
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 - Emesis is contraindicated because cyclohexanone is irritating. DILUTION: If no respiratory compromise is present, administer milk or water as soon as possible after ingestion. Dilution may only be helpful if performed in the first seconds to minutes after ingestion. The ideal amount is unknown; no more than 8 ounces (240 mL) in adults and 4 ounces (120 mL) in children is recommended to minimize the risk of vomiting. GASTRIC LAVAGE: Consider after ingestion of a potentially life-threatening amount of poison if it can be performed soon after ingestion (generally within 1 hour). Protect airway by placement in the head down left lateral decubitus position or by endotracheal intubation. Control any seizures first. ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
MAXIMUM TOLERATED EXPOSURE
Irritation is common at atmospheric concentrations above 50 ppm. Exposure to high concentrations can be expected to produce central nervous system depression (Clayton & Clayton, 1982). In most human subjects, exposure to 25 ppm of the vapor for 5 minutes did not cause effects, while 50 ppm was irritating, especially to the throat. Exposure to 75 ppm resulted in more noticeable eye, nose, and throat irritation (Proctor et al, 1988).
Rabbits exposed to 190 ppm for 6 hours per day for 50 days showed slight liver and kidney injury. At 309 ppm, there was slight conjunctival irritation, while at 1414 ppm, lethargy was observed. At 3082 ppm, effects were incoordination, salivation, labored breathing, narcosis, and some deaths (Proctor et al, 1988). Five of six rats survived exposure to 2000 ppm for 4 hours, but 4000 ppm caused coma and death to all six rats (Proctor et al, 1988). Narcosis, hypothermia, and decreased respiration were observed in guinea pigs exposed to 4000 ppm for 6 hours. Recovery from narcosis was slow, and 3 of 10 animals died within 4 days of exposure (Proctor et al, 1988).
- Carcinogenicity Ratings for CAS108-94-1 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Cyclohexanone 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 Assessed under the IRIS program. ; Listed as: Cyclohexanone 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: Cyclohexanone 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: Cyclohexanone MAK (DFG, 2002): Category 3B ; Listed as: Cyclohexanone Category 3B : Substances for which in vitro or animal studies have yielded evidence of carcinogenic effects that is not sufficient for classification of the substance in one of the other categories. Further studies are required before a final decision can be made. A MAK value can be established provided no genotoxic effects have been detected. (Footnote: In the past, when a substance was classified as Category 3 it was given a MAK value provided that it had no detectable genotoxic effects. When all such substances have been examined for whether or not they may be classified in Category 4, this sentence may be omitted.)
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 CAS108-94-1 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 5 mg/kg-day
Inhalation: Drinking Water:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS108-94-1 (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 CAS108-94-1 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS108-94-1 (National Institute for Occupational Safety and Health, 2007):
Listed as: Cyclohexanone REL: IDLH: IDLH: 700 ppm Note(s): Not Listed
- OSHA PEL Values for CAS108-94-1 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS108-94-1 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS108-94-1 (U.S. Environmental Protection Agency, 2010):
Listed as: Cyclohexanone Final Reportable Quantity, in pounds (kilograms): Additional Information: The following spent non-halogenated solvents and the still bottoms from the recovery of these solvents. (F003) Listed as: Cyclohexanone Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS108-94-1 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS108-94-1 (U.S. Environmental Protection Agency, 2010b):
Listed as: Cyclohexanone P or U series number: U057 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 CAS108-94-1 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS108-94-1 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS108-94-1 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS108-94-1 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1915 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1915 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS108-94-1 (NFPA, 2002):
Listed as: Cyclohexanone Hazard Ratings: Health Rating (Blue): 1 Flammability Rating (Red): 2 Instability Rating (Yellow): 0 Oxidizer/Water-Reactive Designation: Not Listed
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Isolate from ignition sources (OHM/TADS , 1991). Keep in a cool, well-ventilated location (OHM/TADS , 1991).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
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 108-94-1.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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.
Cyclohexanone is flammable when exposed to heat or flame (Sax & Lewis, 1989).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS108-94-1 (NFPA, 2002):
Listed as: Cyclohexanone Flammability Rating: 2
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (ERG, 2004)
Water spray, fog or alcohol-resistant foam. Use water spray or fog; do not use straight streams. Move containers from fire area if you can do it without risk.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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 CAS108-94-1 (NFPA, 2002):
- If cyclohexanone is on fire or involved in fire: Do not extinguish fire unless flow can be stopped. Use water in flooding quantities as fog. Solid streams of water may be ineffective. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Use "alcohol" foam, dry chemical or carbon dioxide (AAR, 1987).
EXPLOSION HAZARD
- Cyclohexanone forms an explosive reaction with nitric acid at 75 degrees C (Sax & Lewis, 1989).
- Reaction with hydrogen peroxide + nitric acid forms an explosive peroxide (Sax & Lewis, 1989).
DUST/VAPOR HAZARD
- Cyclohexanone poses a slight explosion hazard in its vapor form, when exposed to flames (Sax & Lewis, 1989).
- When heated to decomposition, cyclohexanone emits acrid smoke and irritating fumes (Sax & Lewis, 1989).
REACTIVITY HAZARD
- Cyclohexanone can react vigorously with oxidizing materials (Sax & Lewis, 1989).
- Cyclohexanone is incompatible with oxidizers and nitric acid (NIOSH, 1990).
- Cyclohexanone forms an explosive reaction with nitric acid at 75 degrees C (Sax & Lewis, 1989).
- Reaction with hydrogen peroxide + nitric acid forms an explosive peroxide (Sax & Lewis, 1989).
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 127 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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 127 (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.
- AIHA ERPG Values for CAS108-94-1 (AIHA, 2006):
- DOE TEEL Values for CAS108-94-1 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS108-94-1 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS108-94-1 (National Institute for Occupational Safety and Health, 2007):
IDLH: 700 ppm Note(s): Not Listed
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 127 (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 127 (ERG, 2004) At the time of this review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices (HSDB , 1991). Cyclohexanone is a waste chemical stream constituent which may be subjected to ultimate disposal by controlled incineration (HSDB , 1991). Cyclohexanone is a good candidate for fluidized bed incineration at a temperature range of 450 to 980 degrees C and residence times of seconds for liquids and gases, and longer for solids. It is a good candidate for rotary kiln incineration at a temperature range of 820 to 1,600 degrees C and residence times of seconds for liquids and gases, and hours for solids. Cyclohexanone is also a good candidate for liquid injection incineration at a temperature range of 650 to 1,600 degrees C and residence time of 0.1 to 2 seconds (HSDB , 1991). If cyclohexanone is not on fire and not involved in fire: Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. Build dikes to contain flow as necessary. Use water spray to knock-down vapors (AAR, 1987). BIODEGRADATION: The algal strain Chlorella pyreniodosa Chick was shown to reduce cyclohexanone (C6ON) to cyclohexanol. The maximum accumulation of cyclohexanol was generated at 0.2% cyclohexanone (Yoshizako et al, 1992).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Cyclohexanone is emitted to the atmosphere during its industrial production from venting of "spent air" and other vent streams. Use of cyclohexanone as a solvent for lacquers, inks, resins, paint and spot removers, and insecticides results in its evaporation into the air. Cyclohexanone releases in wastewater and air may also occur from its primary use as an intermediate to manufacture nylon (HSDB , 1991).
ENVIRONMENTAL FATE AND KINETICS
OTHER TERRESTRIAL FATE: When released to soil, cyclohexanone can be expected to leach significantly. Its detection in groundwater and in leachate from a waste site indicate that leaching does occur in the environment. Various biological screening studies have found that cyclohexanone is biodegradable in various test systems, including natural water. This suggest that biodegradation in soil is possible. Cyclohexanone on soil surfaces will be susceptible to significant volatilization and photodegradation (HSDB , 1991). AQUATIC FATE: The important environmental fate processes for cyclohexanone in water appear to be biodegradation, photolysis, and volatilization. Various biological screening studies have found that cyclohexanone is biodegradable in various test systems, including natural water. Cyclohexanone photolyzes in ambient air (half-life of about 4.3 days) which suggests that direct photolysis in water is likely to occur; however, the photolysis rate in water will be slower. Volatilization from shallow, rapidly moving streams should be significant (estimated half-life of 3.1 days from a model stream one meter deep); however, volatilization from deeper and less rapidly moving bodies of water such as lakes and ponds will be much slower. Aquatic hydrolysis, bioconcentration, and adsorption to sediment are not important mechanisms of transport (HSDB , 1991). ATMOSPHERIC FATE: Based on a vapor pressure of 5 mmHg at 26.4 degrees C, cyclohexanone should exist almost entirely in the vapor-phase in the ambient atmosphere. It will degrade relatively rapidly by reaction with sunlight-produced hydroxyl radicals (half-life of about 1 day) and by direct photolysis (half-life of about 4.3 days) (HSDB , 1991).
ENVIRONMENTAL TOXICITY
- Effect of low concentrations of cyclohexanone on aquatic life is unknown (CHRIS , 1991).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Cyclohexanone is a water-white to pale-yellow, oily liquid with a peppermint- or acetone-like odor (NIOSH, 1990; (Budavari, 1989).
PH
VAPOR PRESSURE
- 10 mmHg (at 38.7 degrees C) (Sax & Lewis, 1989)
- 135 mmHg (at 100 degrees C) (Sax & Lewis, 1987)
- 5 mmHg (at 26.4 degrees C) (HSDB , 1991)
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
LIQUID: 0.9478 (at 20/4 degrees C) (Budavari, 1989) LIQUID: 0.9421 (at 25/4 degrees C) (Budavari, 1989)
FREEZING/MELTING POINT
-32.1 degrees C (Budavari, 1989) -45.0 degrees C (Sax & Lewis, 1989)
BOILING POINT
- 155.6 degrees C (at 760 mmHg) (Budavari, 1989)
- 132.5 degrees C (at 400 mmHg) (Budavari, 1989)
- 110.3 degrees C (at 200 mmHg) (Budavari, 1989)
- 90.4 degrees C (at 100 mmHg) (Budavari, 1989)
- 77.5 degrees C (at 60 mmHg) (Budavari, 1989)
- 67.8 degrees C (at 40 mmHg) (Budavari, 1989)
- 52.5 degrees C (at 20 mmHg) (Budavari, 1989)
- 38.7 degrees C (at 10 mmHg) (Budavari, 1989)
- 26.4 degrees C (at 5 mmHg) (Budavari, 1989)
- 1.4 degrees C (at 1.0 mmHg) (Budavari, 1989)
FLASH POINT
- 44 degrees C; 111 degrees F (Sax & Lewis, 1989; Sax & Lewis, 1987; NFPA, 1991)
- 63 degrees C; 147 degrees F (closed cup) (Budavari, 1989)
AUTOIGNITION TEMPERATURE
- 420 degrees C; 788 degrees F (Sax & Lewis, 1989; Sax & Lewis, 1987; NFPA, 1991)
EXPLOSIVE LIMITS
SOLUBILITY
150 g/L (at 10 degrees C) (Budavari, 1989) 50 g/L (at 30 degrees C) (Budavari, 1989)
HENRY'S CONSTANT
- 2.56x10(-5) atm-m(3)/mol (Ehrenfeld et al, 1986)
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