DICYCLOPENTADIENE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
DICYCLOPENTADIENE 1,3-CPD DCPD BICYCLOPENTADIENE BISCYCLOPENTADIENE CYCLOPENTADIENE DIMER 1,3-CYCLOPENTADIENE, DIMER alpha-DICYCLOPENTADIENE (endo isomer) 1,3-DICYCLOPENTADIENE DIMER DICYKLOPENTADIEN (Czech) DIMER CYKLOPENTADIENU (Czech) 4,7-METHANOINDENE, 3a,4,7,7a-TETRAHYDRO- 4,7-METHANO-1H-INDENE, 3a,4,7,7a-TETRAHYDRO- 3a,4,7,7a-TETRAHYDRO-4,7-METHANOINDENE TRICYCLO(5,2,1,0)-3,8-DECADIENE
IDENTIFIERS
SYNONYM REFERENCE
- (ACGIH, 1991; (HSDB, 1996); NIOSH , 1996; RTECS , 1996)
USES/FORMS/SOURCES
Dicyclopentadiene is used as a flame retardant for plastics, as a chemical intermediate for chlorinated hydrocarbon insecticides, as a hardener and dryer in linseed as well as soybean oil, as a repellent for animals, and in the production of EPDM elastomers, metallocenes, resins, varnishes, and paints (ACGIH, 1991; Clayton & Clayton, 1994; (HSDB, 1996); Lewis, 1993).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Dicyclopentadiene is an eye, skin, and respiratory tract irritant. High concentrations may cause CNS depression. Ingestion of dicyclopentadiene would likely cause gastrointestinal tract irritation. Headache, sneezing, and cough may occur.
- In experimental animals, exposure has caused eye irritation; loss of coordination; hemorrhage of the lungs, kidney, intestine, stomach, bladder, and the thymus; and convulsions. Chronic exposure in animals has caused kidney damage, chronic pneumonia, and bronchiectasis.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
May cause toxic effects if inhaled or absorbed through skin. Inhalation or contact with material may irritate or burn skin and eyes. Fire will produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control or dilution water may cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. Wash skin with soap and water. Keep victim warm and quiet. In case of burns, immediately cool affected skin for as long as possible with cold water. Do not remove clothing if adhering to skin. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
FIRST AID EYE EXPOSURE - Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Contact lenses should not be worn when working with this chemical. DERMAL EXPOSURE - Immediately flush the contaminated skin with soap and water. If this chemical penetrates the clothing, immediately remove the clothing and flush the skin with water. If irritation persists after washing, get medical attention. INHALATION EXPOSURE - Move the exposed person to fresh air at once. If breathing has stopped, perform artificial respiration. Keep the affected person warm and at rest. Get medical attention as soon as possible. ORAL EXPOSURE - If this chemical has been swallowed, get medical attention immediately. TARGET ORGANS - Eyes, skin, respiratory tract, central nervous system, 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.
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 or CNS depression, 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
MAXIMUM TOLERATED EXPOSURE
In one occupational situation, workers were accidentally exposed to an unknown concentration of dicyclopentadiene vapor for 5 months. Workers complained of headache for the first two months, but were asymptomatic for the following three months despite continued exposure (ACGIH, 1991; Hathaway et al, 1991). In a volunteer study, two subjects were exposed to 1 ppm for seven minutes. This produced mild throat and eye irritation. One subject had olfactory fatigue after 24 minutes. Exposure to 5.5 ppm for 30 minutes produced no olfactory fatigue (ACGIH, 1991; Hathaway et al, 1991).
Animal studies demonstrate a wide sensitivity among various species. Acute toxicity also varies greatly by route of exposure. Most followed a general pattern of symptoms, with eye irritation, loss of coordination, and convulsions leading to death (ACGIH, 1991; Hathaway et al, 1991).
- Carcinogenicity Ratings for CAS77-73-6 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Dicyclopentadiene ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Dicyclopentadiene EPA (U.S. Environmental Protection Agency, 2011): Not Listed IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Dicyclopentadiene 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 CAS77-73-6 (U.S. Environmental Protection Agency, 2011):
CALCULATIONS
CONVERSION FACTORS 1 ppm = 5.49 mg/m(3) ((HSDB, 1996)) 1 ppm = 5.41 mg/m(3) (Clayton & Clayton, 1994) 1 mg/m(3) = 0.18 ppm ((HSDB, 1996))
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS77-73-6 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
- AIHA WEEL Values for CAS77-73-6 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS77-73-6 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS77-73-6 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS77-73-6 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS77-73-6 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS77-73-6 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS77-73-6 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS77-73-6 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS77-73-6 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Dicyclopentadiene Effective Date for Reporting Under 40 CFR 372.30: 1/1/95 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS77-73-6 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS77-73-6 (EPA, 2005):
Listed as: 4,7-Methano-1H-indene, 3a,4,7,7a-tetrahydro-
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2048 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN2048 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS77-73-6 (NFPA, 2002):
-HANDLING AND STORAGE
HANDLING
- According to 49 CFR 171.2: "No person may /transport,/ offer or accept a hazardous material for transportation in commerce unless that material is properly classed, described, packaged, marked, labeled, and in condition for shipment as required or authorized by.../the hazardous materials regulations (49 CFR 171 to 177)" ((HSDB, 1996)).
- This compound is stable during transport ((CHRIS, 1996)).
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Dicyclopentadiene should be stored in a cool, ventilated location. Conditions should be periodically inspected ((HSDB, 1996)). Storage temperature should be ambient ((CHRIS, 1996)). Open flame arrester venting should be utilized ((CHRIS, 1996)).
This compound should be isolated from oxidizers, direct sunlight, and any fire hazard ((HSDB, 1996)).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
- Persons handling dicyclopentadiene should wear a face shield, rubber gloves, work clothing, as well as an all-purpose canister mask (ITI, 1988).
- Appropriate protective clothing should be worn to prevent skin contact. If skin contact occurs, washing with copious amounts of soap and water should be done immediately. Avoid contact with the vapor. Contaminated or wet clothing should be removed and replaced. In addition, persons working with this compound should change into uncontaminated clothing before leaving the job site (AAR, 1994; (NIOSH , 1996).
EYE/FACE PROTECTION
- Use appropriate eye protection to prevent contact with this substance. In areas where there is any possibility that persons may be exposed to dicyclopentadiene, eyewash fountains should be provided (NIOSH , 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 77-73-6.
ENGINEERING CONTROLS
- A facility for quickly drenching the body, or body parts, with water needs to be provided within the immediate work area. This is intended to quickly remove dicyclopentadiene from any body areas likely to be exposed. In some instances a hose connected to a sink may be permissible, in others a full deluge shower may be required (NIOSH , 1996).
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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.
Dicyclopentadiene is combustible in its liquid and solid states; it is a fire hazard when exposed to flame or heat (Lewis, 1992; Lewis, 1993; NIOSH , 1996). When in solid form, this compound will sink in water, when in liquid form it will float in a slick (OHM/TADS , 1996). It can flashback along a vapor trail ((CHRIS, 1996)). Dicyclopentadiene releases acrid fumes and smoke when heated to decomposition (Lewis, 1992).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS77-73-6 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (ERG, 2004)
Water spray, fog or regular foam. Do not use straight streams. Move containers from fire area if you can do it without risk.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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 CAS77-73-6 (NFPA, 2002):
- When fighting a fire involving dicyclopentadiene utilize alcohol foam, carbon dioxide, or dry chemical. Water may be ineffective, and solid streams of water may actually spread the fire. Water fog or spray may be employed to cool threatened containers/structures. Apply from as great a distance as is possible. Unless the leak can be confined or stopped, do not attempt to extinguish a fire involving this compound (AAR, 1994; ((CHRIS, 1996); OHM/TADS , 1996; Lewis, 1992).
EXPLOSION HAZARD
- Dicyclopentadiene vapor can explode if ignited within an enclosed area ((CHRIS, 1996)).
DUST/VAPOR HAZARD
- This compound emits acrid fumes and smoke when heated to decomposition (Lewis, 1992).
REACTIVITY HAZARD
- Dicyclopentadiene releases acrid fumes and smoke when heated to decomposition (Lewis, 1992).
- It is incompatible with oxidizers (Lewis, 1992; NIOSH , 1996).
- This compound is non-corrosive ((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 130 (ERG, 2004)
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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 130 (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 CAS77-73-6 (AIHA, 2006):
Listed as Dicyclopentadiene ERPG-1 (units = ppm): 0.01 ERPG-2 (units = ppm): 5 ERPG-3 (units = ppm): 75 Under Ballot, Review, or Consideration: No Definitions: ERPG-1: The ERPG-1 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed for up to one hour without experiencing more than mild, transient adverse health effects or perceiving a clearly defined objectionable odor. ERPG-2: The ERPG-2 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed for up to one hour without experiencing or developing irreversible or other serious health effects or symptoms that could impair an individual's ability to take protective action. ERPG-3: The ERPG-3 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed for up to one hour without experiencing or developing life-threatening health effects.
- DOE TEEL Values for CAS77-73-6 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Dicyclopentadiene TEEL-0 (units = ppm): 0.01 TEEL-1 (units = ppm): 0.01 TEEL-2 (units = ppm): 5 TEEL-3 (units = ppm): 75 Definitions: TEEL-0: The threshold concentration below which most people will experience no adverse health effects. TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure. TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape. TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.
- AEGL Values for CAS77-73-6 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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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 CAS77-73-6 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 130 (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 130 (ERG, 2004) Keep ignition sources out of the area. If possible, stop the leak. Employ water spray to keep vapors down. Utilize dikes to contain the spill. Make sure this material stays out of sewers and water sources (AAR, 1994). For in situ amelioration (in bodies of water), if in solid form utilize a dredge; if in liquid form use oil skimming equipment in conjunction with sorbent foams to treat the slick (OHM/TADS , 1996).
Small quantities, collected on a piece of paper, should be placed on an iron plate and burned within a fume hood. Larger amounts may be placed in a package stuffed with a flammable material and burned in a furnace (or) dissolved in a combustible solvent and then sprayed into a furnace for incineration (ITI, 1988; OHM/TADS , 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
- Dicyclopentadiene, undoubtedly, enters the environment from its production and use. It is not known to occur in nature ((HSDB, 1996)).
ENVIRONMENTAL FATE AND KINETICS
When released to the atmosphere, dicyclopentadiene will likely react with photochemically produced hydroxyl radicals; the half-life for this process is estimated to be 3.1 hours. Another important route is destruction via the gas phase reaction with ozone; estimated half-life of 48 minutes. Wet and dry deposition as well as direct photochemical degradation are not thought to be important routes ((HSDB, 1996)).
SURFACE WATER Volatilization is the primary fate process in water; estimated half-life from a model river of 3.4 hours. Reaction with photochemically produced oxidants may also be important. Adsorption to suspended organic matter and sediment may be significant. Biodegradation, direct photolysis, and hydrolysis are not major routes ((HSDB, 1996)).
TERRESTRIAL Volatilization from surface soil may be quite rapid, although this process may be slowed by dicyclopentadiene's adsorption to the soil. This compound is expected to display low mobility. Biodegradation and hydrolysis are not expected to be significant factors ((HSDB, 1996)).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- LC50, Cyprinus carpio (carp), 62.2 mg/L/96 hr ((HSDB, 1996))
- LC50, Salmo gairdneri (rainbow trout), 22.86 mg/L/96 hr ((HSDB, 1996))
- LC50, Salmo gairdneri (rainbow trout), 42.3 mg/L/96 hr ((HSDB, 1996))
- LC50, Lepomis macrochirus (bluegill), 75.2 mg/L/96 hr ((HSDB, 1996))
- LC50, Daphnia species (water flea), 6.9 mg/L/48 hr ((HSDB, 1996))
- ECSO (inhibition of cell multiplication), Tetrahymena pyriformis (ciliate protozoan), 5.3 mg/L/24 hr ((HSDB, 1996))
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- At room temperature dicyclopentadiene exists as colorless crystals; it is a liquid above 90 degrees F. It possesses an odor variously described as sweet, sharp, disagreeable, and camphor-like (ACGIH, 1991; Clayton & Clayton, 1994; (HSDB, 1996); Lewis, 1992).
VAPOR PRESSURE
- 60 mmHg (at 88 degrees C) (OHM/TADS , 1996)
- 10 mmHg (at 47.6 degrees C) (Clayton & Clayton, 1994; Lewis, 1992)
- 1.4 mmHg (at 20 degrees C) ((HSDB, 1996))
SPECIFIC GRAVITY
- OTHER TEMPERATURE AND/OR PRESSURE
LIQUID: 0.979 (at 20/20 degrees C) (ITI, 1988; Lewis, 1993) 0.9302 (at 35/4 degrees C) ((HSDB, 1996))
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
0.976 g/mL (at 35 degrees C) (ACGIH, 1991) Lewis, 1992) 0.9302 g/mL (at 20 degrees C) (Clayton & Clayton, 1994) LIQUID: 0.98 g/mL (at 95 degrees F) (NIOSH , 1996) LIQUID: 0.978 g/mL (at 20 degrees C) ((CHRIS, 1996))
FREEZING/MELTING POINT
35 degrees C; 95 degrees F (Clayton & Clayton, 1994) 90 degrees F (NIOSH , 1996)
32 degrees C (Clayton & Clayton, 1994) 32.9 degrees C (Lewis, 1992) 33.6 degrees C (ACGIH, 1991; Lewis, 1993) 91 degrees F (NFPA, 1994)
BOILING POINT
- Dicyclopentadiene depolymerizes at its boiling point, forming two molecules of cyclopentadiene (NIOSH , 1996).
166.6 degrees C (Lewis, 1992) 170 degrees C; 338 degrees F; 443 degrees K (ACGIH, 1991; (CHRIS, 1996)) 172 degrees C; 342 degrees F (Lewis, 1993; NFPA, 1994) 64-65 degrees C (at 14 mmHg) ((HSDB, 1996))
FLASH POINT
- 32.2 degrees C; 90 degrees F (open cup) (Lewis, 1993; NIOSH , 1996)
AUTOIGNITION TEMPERATURE
- 503 degrees C; 937 degrees F (NFPA, 1994)
- 941 degrees F ((CHRIS, 1996))
EXPLOSIVE LIMITS
SOLUBILITY
Dicyclopentadiene is practically insoluble in water (Clayton & Clayton, 1994; Lewis, 1993). 0.020 lb dicyclopentadiene/100 lb water (at 68.02 degrees F) (0.02%) ((HSDB, 1996); NIOSH , 1996)
This compound is soluble in acetic acid, acetone, alcohol (greater than 10%), dichloromethane, ether (greater than 10%), ethyl acetate, n-hexane and toluene (Clayton & Clayton, 1994; (HSDB, 1996); Lewis, 1993).
OCTANOL/WATER PARTITION COEFFICIENT
- Log Kow = 2.89 (estimate) ((HSDB, 1996))
HENRY'S CONSTANT
- 0.0107 atm m(3)/mol (at 25 degrees C) (estimated) ((HSDB, 1996))
OTHER/PHYSICAL
1.5073 (at 31 degrees C) (Lewis, 1993) 1.5050 (at 20 degrees C) (Clayton & Clayton, 1994)
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