ISODRIN
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
ISODRIN COMPOUND 711 1,4:5,8-DIMETHANONAPHTHALENE, 1,2,3,4,10,10- HEXACHLORO-1,4,4a,5,8,8a-HEXAHYDRO-, endo, endo- 1,4:5,8-DIMETHANONAPHTHALENE, 1,2,3,4,10,10- HEXACHLORO-1,4,4a,5,8,8a-HEXAHYDRO-, (1 alpha, 4 alpha, 4a beta, 5 beta, 8 beta, 8a beta)- EXPERIMENTAL INSECTICIDE 711 1,2,3,4,10,10-HEXACHLORO-1,4,4A,5,8,8A-HEXAHYDRO- endo, endo-1,4:5,8-DIMETHANONAPHTHALENE 1,2,3,4,10,10-HEXACHLORO-1,4,4a,5,8,8a-HEXAHYDRO- 1,4:5,8-endo-endo-DIMETHANONAPHTHALENE 1,2,3,4,10,10-HEXACHLORO-1,4,4a,5,8,8a-HEXAHYDRO- 1,4-endo, endo-5,8-DIMETHANONAPHTHALENE LATKA 711 (Czech) SD 3418
IDENTIFIERS
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures.
SYNONYM REFERENCE
- (EPA, 1985; HSDB , 1990; RTECS , 1990)
USES/FORMS/SOURCES
Isodrin is a chlorinated hydrocarbon insecticide in the cyclodiene family; it is an isomer of aldrin (Sax & Lewis, 1987). It occurs as a crystalline solid which is soluble in ether, acetone, alcohol, and benzene (HSDB, 1993).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Isodrin is a chlorinated hydrocarbon insecticide in the chlorinated ethane/cyclodiene/hexachlorocyclohexane family. This review is based on the properties of chlorinated hydrocarbon insecticides in general, with effects specific to isodrin identified. The primary target of action is the central nervous system. CNS excitation and seizures may occur. Respiratory depression may occur concurrently with coma and is a common cause of death.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Highly toxic, may be fatal if inhaled, swallowed or absorbed through skin. 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.
ACUTE CLINICAL EFFECTS
- From its acute oral LD50 of 7 mg/kg in rats, isodrin is an EXTREMELY TOXIC substance (Morgan, 1989). Isodrin can be absorbed by inhalation, ingestion, and skin contact (EPA, 1985). It is a skin irritant and can cause rashes and acne (HSDB, 1993; (Sax & Lewis, 1989).
- Signs and symptoms of acute isodrin poisoning resemble those of dieldrin and aldrin. Nausea, vomiting, dizziness, headache, tremors, seizures, coma, hypertension, fever, tachycardia, and behavioral alterations may occur (EPA, 1985) HSDB, 1993).
- Cyclodiene chlorinated hydrocarbon insecticides are respiratory depressants and CNS excitants and convulsants. Seizures may occur early and may recur over several days following acute exposure. Clonic jerking has been reported with aldrin exposure. Metabolic acidosis may result from seizures (Clinical Note, 1984; EPA, 1985; Proctor et al, 1988; Morgan, 1989).
- Nausea, vomiting, diarrhea, elevated serum levels of liver enzymes, and hepatic necrosis may occur from exposure to chlorinated hydrocarbon insecticides (Clayton & Clayton, 1981; Proctor et al, 1988) HSDB, 1993; (Sax & Lewis, 1989). Skin irritation may result from extensive contact with these agents or with the petroleum distillates in which they are suspended. Dermatitis is unusual; however, erythematobullous dermatitis has been reported. Generally, only minor erythema is caused by pure aldrin. Commercial formulations may contain more irritating components (Clayton & Clayton, 1981; Proctor et al, 1988).
- Such compounds are very toxic because they are LIPOPHILIC -- high fat solubility makes the nervous system a major target organ (ILO, 1983).
CHRONIC CLINICAL EFFECTS
- Because isodrin is lipid-soluble and may accumulate in body fat, CUMULATIVE TOXICITY may occur with repeated exposure (Finkel, 1983).
- Neurologic effects of chronic isodrin exposure are expected to be similar to those of acute exposure. EEG changes were seen in the absence of any other signs or symptoms in one group of workers exposed to isodrin (Hoogendam et al, 1962).
- Symptoms of chronic cyclodiene chlorinated hydrocarbon insecticide exposure include CNS excitement, EEG abnormalities, and seizures. No permanent disabilities were found in aldrin workers who had experienced seizures (Hoogendam et al, 1962; Kazantzis et al, 1964; Hoogendam et al, 1965; Gupta, 1975; Baselt & Cravey, 1989).
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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.
GENERAL Move victim to fresh air; call for emergency care. If not breathing, give artificial respiration. If breathing is difficult, give oxygen (EPA, 1985).
DECONTAMINATION In case of contact with isodrin, immediately flush skin or eyes with running water for at least 15 minutes. Speed in removing material from skin is of extreme importance. Remove and isolate contaminated clothing and shoes at the site (EPA, 1985).
DELAYED EFFECTS 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. 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). First responders should wear protective clothing to prevent secondary contamination. Be prepared to collect any vomitus or excreta in a manner to prevent further contamination; bag and treat as hazardous waste. 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.
REFRACTORY SEIZURES: Consider continuous infusion of midazolam, propofol, and/or pentobarbital. Hyperthermia, lactic acidosis and muscle destruction may necessitate use of neuromuscular blocking agents with continuous EEG monitoring. Do not give oils by mouth. Do not administer adrenergic amines, which may further increase myocardial irritability and produce refractory ventricular arrhythmias. CHOLESTYRAMINE - Oral administration may enhance the excretion of kepone and chlordane which are trapped in the enterohepatic circulation. Dialysis, exchange transfusion, and hemoperfusion are probably ineffective.
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). First responders should wear protective clothing to prevent secondary contamination. Be prepared to collect any vomitus or excreta in a manner to prevent further contamination; bag and treat as hazardous waste. 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.
REFRACTORY SEIZURES: Consider continuous infusion of midazolam, propofol, and/or pentobarbital. Hyperthermia, lactic acidosis and muscle destruction may necessitate use of neuromuscular blocking agents with continuous EEG monitoring. Do not give oils by mouth. Do not administer adrenergic amines, which may further increase myocardial irritability and produce refractory ventricular arrhythmias. CHOLESTYRAMINE - Oral administration may enhance the excretion of kepone and chlordane which are trapped in the enterohepatic circulation. Dialysis, exchange transfusion, and hemoperfusion are probably ineffective.
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. 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). Treatment should include recommendations listed in the INHALATION EXPOSURE section when appropriate.
ORAL 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). 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.
REFRACTORY SEIZURES: Consider continuous infusion of midazolam, propofol, and/or pentobarbital. Hyperthermia, lactic acidosis and muscle destruction may necessitate use of neuromuscular blocking agents with continuous EEG monitoring. 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. Do not give oils by mouth. Do not administer adrenergic amines, which may further increase myocardial irritability and produce refractory ventricular arrhythmias. CHOLESTYRAMINE: Oral administration may enhance the excretion of kepone and chlordane which are trapped in the enterohepatic circulation. Dialysis, exchange transfusion, and hemoperfusion are probably ineffective.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
From its acute oral toxicity in animals, isodrin would be considered in the EXTREMELY TOXIC group of organochlorine insecticides (EPA, 1985). The probable oral lethal dose for humans is in the range of 5 to 50 mg/kg (between 7 drops and 1 teaspoon for a 150-pound person)(EPA, 1985).
MAXIMUM TOLERATED EXPOSURE
- Carcinogenicity Ratings for CAS465-73-6 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed 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 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 CAS465-73-6 (U.S. Environmental Protection Agency, 2011):
References: RTECS, 1998 LD50- (ORAL)MOUSE: LD50- (ORAL)RAT: LD50- (SKIN)RAT:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS465-73-6 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS465-73-6 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS465-73-6 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS465-73-6 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS465-73-6 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS465-73-6 (U.S. Environmental Protection Agency, 2010):
Listed as: 1,4:5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro- 1,4,4a,5,8,8a-hexahydro-, (1alpha,4alpha,4abeta, 5beta,8beta,8abeta)- Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Isodrin Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS465-73-6 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS465-73-6 (U.S. Environmental Protection Agency, 2010b):
Listed as: 1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexa- chloro-1,4,4a,5,8,8a-hexahydro-,(1alpha,4alpha,4abeta,5beta,8beta,8abeta)- P or U series number: P060 Footnote: Listed as: Isodrin P or U series number: P060 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 CAS465-73-6 (U.S. Environmental Protection Agency, 2010):
Listed as: Isodrin Reportable Quantity, in pounds: 1 Threshold Planning Quantity, in pounds: Note(s): Not Listed
- EPA SARA Title III, Community Right-to-Know for CAS465-73-6 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Isodrin Effective Date for Reporting Under 40 CFR 372.30: Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28: 10 Listed as: Isodrin 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 CAS465-73-6 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS465-73-6 (EPA, 2005):
Listed as: 1,4:5,8-Dimethanonaphthalene, 1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-, (1R,4S,4aS,5R,8S,8aR)-rel-
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions (49 CFR 172.101, 2005):
- ICAO International Shipping Name (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS465-73-6 (NFPA, 2002):
-HANDLING AND STORAGE
HANDLING
- Isodrin is not a stable molecule (HSDB , 1991).
- Consult Title 49 CFR, Transportation, Parts 100-180 before shipping hazardous materials (HSDB , 1991).
STORAGE
- ROOM/CABINET RECOMMENDATIONS
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- Isodrin is very toxic, so skin and inhalation contact must be avoided. Wear approved respiratory protection and chemical protective clothing.
- Use dust- and splash-proof safety goggles where there is possibility of contacting the eyes. Wear impervious clothing, gloves, face shields to prevent skin contact (HSDB , 1991).
- Non-impervious clothing which becomes contaminated should be removed immediately and not reworn until the toxin is removed from the clothing. If an employee's clothing has had any possibility of being contaminated, employees should change into uncontaminated clothing before leaving the work premises. Clothing which has had any possibility of being contaminated should be placed in closed containers for storage until it can be discarded or until provision is made for the removal of the material from the clothing (HSDB , 1991).
- Where there is the possibility of exposure to an employee's body, quick drenching showers must be provided within the immediate work area for emergency use (HSDB , 1991).
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 465-73-6.
-PHYSICAL HAZARDS
FIRE HAZARD
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures. POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Non-combustible, substance itself does not burn but may decompose upon heating to produce corrosive and/or toxic fumes. Containers may explode when heated. Runoff may pollute waterways.
To extinguish use water spray, dry chemical, foam, or carbon dioxide (EPA, 1985). Isodrin releases toxic chlorine containing gaseous substances when heated to decomposition (Sax & Lewis, 1989).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS465-73-6 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material. Use water spray or fog; do not use straight streams.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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. 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 CAS465-73-6 (NFPA, 2002):
- This material may burn but will not ignite readily (EPA, 1985).
- Extinguish fire using agent suitable for type of surrounding fire (HSDB , 1991).
- Extinguish by water spray, dry chemical, "alcohol" foam, or carbon dioxide (methods for aldrin related compounds) (HSDB , 1991; EPA, 1985).
- Wear full protective clothing include positive-pressure breathing apparatus (EPA, 1985).
- Move container from fire area if you can do so without risk (EPA, 1985).
- Dike fire control water for later disposal (EPA, 1985).
- Container may explode in heat of fire (EPA, 1985).
When heated to decomposition, isodrin releases toxic chlorine containing gaseous substances (EPA, 1985; Sax & Lewis, 1989). Fire and runoff from fire control may produce irritating or poisonous gases (EPA, 1985). Decomposes at temperatures greater than 100 degrees C (HSDB , 1991)
EXPLOSION HAZARD
- Container may explode in heat of fire (EPA, 1985).
- Material will burn but will not ignite readily (EPA, 1985).
DUST/VAPOR HAZARD
- Fire and runoff from fire control may produce irritating or poisonous gases (EPA, 1985).
REACTIVITY HAZARD
- Isodrin is unstable (EPA, 1985).
- Reactions induced by light or acid (EPA, 1985).
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 151 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 25 to 50 meters (80 to 160 feet) in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (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 151 (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.
- Stay upwind; keep out of low areas (EPA, 1985).
- Ventilate closed spaced before entering them (EPA, 1985).
- Wear positive pressure breathing apparatus and special protective clothing (EPA, 1985).
- Remove and isolate contaminated clothing at the site (EPA, 1985).
- If water pollution occurs, notify local authorities (HSDB , 1991).
- AIHA ERPG Values for CAS465-73-6 (AIHA, 2006):
- DOE TEEL Values for CAS465-73-6 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Isodrin TEEL-0 (units = mg/m3): 1.25 TEEL-1 (units = mg/m3): 4 TEEL-2 (units = mg/m3): 7 TEEL-3 (units = mg/m3): 7 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 CAS465-73-6 (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; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; United States Environmental Protection Agency Office of Pollution Prevention and Toxics, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS465-73-6 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) 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. Cover with plastic sheet to prevent spreading. 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 151 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
Do not touch spilled material. Stop leak if it can be done without risk (EPA, 1985). Dike area far ahead of spill for later disposal (EPA, 1985). Take up with sand or other noncombustible material and place into containers for later disposal (EPA, 1985). Carbon or peat may be used as sorbents (OHM/TADS , 1991). Small Dry Spills: With clean dry shovel place material into clean, dry containers and cover; move containers from spill area (EPA, 1985). If water pollution occurs, notify local authorities (HSDB , 1991).
"At the time of this review, criteria for land treatment or burial disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue, contact environmental regulatory agencies." (HSDB , 1991) Group I Containers: Combustible containers from organic or metallo-organic pesticides should be disposed of in pesticide incinerators or in specified landfill sites (HSDB , 1991). Groups II Containers: Non-combustible containers from organic or metallo-organic pesticides must first be triple-rinsed. Containers that are in good condition may be returned to the manufacturer or formulator of the product, or to a drum reconditioner for reuse with the same type of pesticide product, if such reuse is legal under Dept of Transportation regulations. Containers that are not reused should be punctured and transported to a scrap metal facility for recycling, disposal or burial in a designated landfill (HSDB , 1991). Incineration: A potential candidate for rotary kiln incineration at a temperature range of 820 to 1600 degrees C and residence times of seconds for liquids and gases, and hours for solids (HSDB , 1991). Incineration: A potential candidate for fluidized bed incineration at a temperature range of 450 to 980 degrees C and residence times of econds for liquids and gases, and longer for solids (HSDB , 1991).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Isodrin is no longer manufactured or used commercially in the US (HSDB , 1991).
- Disposal may result in environmental contamination (HSDB , 1991).
- Water uses threatened: fisheries, potable supply, recreation (OHM/TADS , 1991)
ENVIRONMENTAL FATE AND KINETICS
OTHER SOIL: Isodrin undergoes microbial oxidation to endrin by a mechanism analogous the biooxidation of aldrin to dieldrin. The mobility of isodrin in soil may range from moderately mobile to immobile and isodrin is not expected to hydrolyze in moist soils or volatilize from soil surfaces. Based on experimental data, the half-life of isodrin in soil has been estimated to range from 0.5 years to a maximum of 6 years (HSDB , 1991). WATER: Isodrin may bioconcentrate in aquatic organisms, adsorb to suspended solids and sediments, volatilize (calculated half-life 5.4 days in rivers) and undergo very slow microbial transformation to endrin. Isodrin is not expected to hydrolyze since it contains no hydrolyzable functional groups (HSDB , 1991). AIR: Isodrin in sunlight may possibly form photoisodrin or isodrin vapor and may react with photochemically generated hydroxyl radicals (calculated vapor-phase half-life 35.5 minutes) (HSDB , 1991).
ENVIRONMENTAL TOXICITY
- Very toxic to aquatic organisms
- BIOACCUMULATION: Known to convert to epoxides found in body fat. Accumulates faster than most halogenated hydrocarbons (OHM/TADS , 1991).
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
VAPOR PRESSURE
FREEZING/MELTING POINT
BOILING POINT
FLASH POINT
EXPLOSIVE LIMITS
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