ETHYLENE DIBROMIDE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
AADIBROOM AETHYLENBROMID (German) AI3-15349 alpha, beta-DIBROMOETHANE BROMOFUME BROMURO di ETILE (Italian) CELMIDE DBE 1,2-DIBROMOETANO (Italian) DIBROMOETHANE 1,2-DIBROMAETHAN (German) 1,2-DIBROMOETHANE sym-DIBROMOETHANE DIBROMURE d'ETHYLENE (French) 1,2-DIBROOMETHAAN (Dutch) DOWFUME 40 DOWFUME EDB DOWFUME W-8 DOWFUME W-10 DOWFUME W-15 DOWFUME W-40 DOWFUME W-85 DOWFUME W-90 DOWFUME W-100 DWUBROMOETAN (Polish) EDB EDB-85 E-D-BEE ETHANE, 1,2-DIBROMO- ETHYLENE BROMIDE ETHYLENE DIBROMIDE 1,2-ETHYLENE DIBROMIDE FUMO-GAS GLYCOL BROMIDE GLYCOL DIBROMIDE ISCOBROME D KOPFUME NEFIS NEPHIS PESTMASTER PESTMASTER EDB-85 SANHYUUM SOILBROM SOILBROM-40 SOILBROM-85 SOILBROM-90 SOILBROM-90EC SOILBROM-100 SOILBROME-85 SOILFUME UNIFUME EDB (ETHYLENE DIBROMIDE)
IDENTIFIERS
4909166 - Ethylene dibromide-methyl bromide mixture, liquid (insecticides, agricultural, not elsewhere classified, liquid) 4940335 - Ethylene dibromide
SYNONYM REFERENCE
- (CHRIS , 1999; HSDB , 1999; Lewis, 1996; RTECS , 1999)
USES/FORMS/SOURCES
Ethylene dibromide is used as an antiknock additive in gasoline and as a soil/grain fumigant (Ashford, 1994). This compound is also used as an agricultural fumigant and industrial chemical. However, most agricultural uses have been banned in the United States since 1984 (Lewis, 1998). Ethylene dibromide is used as a scavenger for lead in gasoline, as a grain fumigant, as a general solvent, and as a fumigant for tree crops. It is also used for waterproofing preparations, and in the synthesis of dyes, pharmaceuticals, and other brominated compounds (ACGIH, 1991; Hathaway et al, 1996; Lewis, 1993). This compound is used as a fumigant for ground pest control and as a constituent of ethyl gasoline. It may also be used in gauge fluids, fire extinguishers, in waterproofing preparations, and may be used as a solvent for celluloid, fats, oils, and waxes (Sittig, 1991). Ethylene dibromide is made from ethylene and bromine and can also be made from acetylene and hydrogen bromide (HBr) (Budavari, 1996). Emulsifiable ethylene dibromide weighs 18.1 lbs/gallon (AAR, 1996). Ethylene dibromide was banned from use for grain products and as a soil fumigant in the US in 1984 (Press Release, 1984). Due to its low flammability in air, ethylene dibromide has been used as a fire extinguishing agent (Clayton & Clayton, 1994).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Ethylene dibromide is toxic following ingestion, inhalation, and dermal contact. Rapid effects following ingestion are similar to those following inhalation of concentrated vapors and can include altered gastrointestinal motility, nausea, vomiting, dizziness, drowsiness, agitation, decreased urine output or anuria, chest pain, cough, and respiratory distress. Severe ingestions have resulted in acute hepatic and renal failure, metabolic acidosis and coagulopathy.
Unconsciousness and coma have occurred after brief inhalation exposure to vapors in confined spaces. Eye, mucous membrane, and respiratory tract irritation with pneumonia and delayed pulmonary edema can result from vapor inhalation.
- Renal and hepatic damage or failure have resulted from ingestion and inhalation exposures in humans, and are suspected to occur following other routes of exposure, based on experimental animal studies. Cardiac arrest, and/or multiorgan failure have occurred in fatal cases and may result secondarily from hepatic necrosis, massive fluid losses, and/or electrolyte imbalance. Respiratory arrest can occur. Hypoglycemia, acidosis, and hematologic abnormalities have also been reported.
- Liquid ethylene dibromide is an eye, mucous membrane, and skin irritant. Brief skin contact will cause erythema and discomfort. Blistering can result if the skin is not rapidly decontaminated. Chemical burns/blisters can occur following prolonged dermal exposure, especially if the site of contact is covered in a fashion which inhibits vaporization. Ethylene dibromide can be absorbed through the skin to produce systemic effects.
- One study has shown adverse effects on the sperm of workers exposed to ethylene dibromide. Oral administration of ethylene bromide has been associated with testicular atrophy, abnormal sperm, and decreased sperm production in experimental animals.
- Irritating bromide fumes can be released if ethylene dibromide is heated to decomposition.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004)
TOXIC; inhalation, ingestion or skin contact with material may cause severe injury or death. Contact with molten substance may cause severe burns to skin and eyes. Avoid any skin contact. Effects of contact or inhalation may be delayed. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
ACUTE CLINICAL EFFECTS
- Ethylene dibromide (EDB) is quite toxic in humans. A dose of 4.5 mL was fatal when ingested; liver and kidney damage were evident at autopsy (ILO, 1983; ACGIH, 1991). There have been industrial fatalities (Letz et al, 1984). EDB is readily absorbed by the oral, inhalation, or dermal exposure routes (HSDB, 2004; Hayes & Laws, 1991a). Symptoms depend somewhat on the exposure route (ILO, 1983). Concentrations of EDB sufficient to induce anesthesia are usually lethal (ACGIH, 1991).
- Liquid EDB is a severe skin, mucous membrane, and eye irritant, producing blistering and ulceration (ILO, 1983; HSDB, 2004; Hathaway et al, 1991). Inhalation produces lung damage, congestion, pulmonary edema, chemical pneumonia, and CNS depression.
- Symptoms of CNS depression include nausea, headache, weakness, dizziness, loss of coordination and judgement, coma, and death in respiratory failure. When taken orally, EDB can cause liver and kidney damage, vomiting, and excitement and other CNS effects (ILO, 1983).
- Of two men exposed to 0.1% to 0.3% EDB solution inside a tank, one was intermittently comatose and the other was combative and delirious. One died from cardiopulmonary arrest 12 hours after exposure, and the other of progressive liver damage and renal failure after 64 hours. Because the airborne level in the tank of 28 ppm was not deemed sufficiently high to account for the fatalities, they were attributed to dermal exposure of the solution in the tank (Hathaway et al, 1991; Hayes & Laws, 1991; Letz et al, 1984).
- Death from acute exposure to EDB is usually from pneumonia secondary to lung injury (Clayton & Clayton, 1994).
- EDB is metabolized by the cytochrome P450 system. Of 10 human P450 isozymes expressed in vitro, only CYP2E1, CYP2A6 and CYP2B6 metabolized EDB. Studies with specific inhibitors of CYP2E1 led to the tentative conclusion that this cytochrome is mainly responsible for the oxidation of EDB in humans (Wormhoudt et al, 1996). The main metabolite of the cytochrome P450 system is bromoacetaldehyde, but the hepatotoxicity and mutagenicity are evidently due to S-2-bromoethylglutathione, formed in the cytosolic fraction (Hayes & Laws, 1991).
CHRONIC CLINICAL EFFECTS
- In an industry-wide exposure study, NIOSH found that typical airborne EDB concentrations range from 10 to 500 ppb during manufacture, approximately 200 ppb in antiknock blending (p 16), and 0 to 80 ppb in agricultural fumigation (Ter Harr, 1980). An occupational mortality study of EDB-exposed workers inconclusive (Ott et al, 1980).
- Ethylene dibromide has been reported to be a skin sensitizer (Hathaway et al, 1991).
- Inhalation of an airborne concentration of 3 to 75 ppm for 13 weeks produced damage of the nasal cavity, trachea, lungs, testes, liver, and kidneys in rats and mice (Reznik, 1980).
-FIRST AID
FIRST AID AND PREHOSPITAL TREATMENT
- Prevent exposure of rescuers and other individuals - refer to PREVENTION OF CONTAMINATION.
Ingestion of these compounds may result in burns of the oropharynx. Emesis is NOT recommended. Rinse the victim's mouth. If spontaneous vomiting is occurring, assist the victim to adopt a position that will maintain an open airway and prevent aspiration. Leaning forward or placing on the left side may be useful.
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 (Caravati, 2004).
- Move the victim out of the contaminated area and to fresh air. If the victim is not responsive, activate the emergency response system. If the victim is not breathing but has a pulse, administer artificial respiration. If the victim is pulseless, administer CPR. If the victim has difficulty in breathing, administer humidified oxygen, if available.
- DERMAL/EYE: Remove contaminated clothing, jewelry, and shoes. Immediately wash contaminated skin, hair, and under the nails with soap and copious amounts of water. Flush contaminated eyes with running water for at least 15 minutes. Prompt removal of contaminated items and dermal/eye decontamination is of extreme importance in order to prevent severe local and systemic effects. After decontamination, lightly cover skin burns with dry sterile dressings. Contaminated items should be isolated in sealed containers, away from light, heat, active metals, and liquid ammonia.
- Keep the victim quiet and maintain normal body temperature. Observe for delayed effects. Central nervous system depression, respiratory distress, and cardiac disturbances may develop and necessitate resuscitation efforts or continued support to prevent aspiration.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance; give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
FIRST AID EYE EXPOSURE: Immediately wash the eyes with large amounts of water, occasionally lifting the lower and upper lids. Get medical attention immediately. Contact lenses should not be worn when working with this chemical. DERMAL EXPOSURE: Immediately wash the contaminated skin with soap and water. If this chemical penetrates the clothing, immediately remove the clothing, wash the skin with soap and water, and get medical attention promptly. INHALATION EXPOSURE: Move the exposed person to fresh air at once. If breathing has stopped, perform artificial respiration. Keep the affected person warm and at rest. Get medical attention as soon as possible. ORAL EXPOSURE: If this chemical has been swallowed, get medical attention immediately. TARGET ORGANS: Eyes, skin, respiratory system, liver, kidneys, reproductive system (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. 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. DIMERCAPROL (BAL) THERAPY should be considered in life-threatening cases as a means of limiting sulfhydryl enzyme inhibition but has not been critically tested in controlled studies.
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. 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. 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. 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. 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
INHALATION GENERAL - The low vapor pressure of ethylene dibromide and increased care in its use appear to limit the number of human cases of toxic inhalational exposures in the workplace (Torkelson, 1994). Use of ethylene dibromide in confined spaces without appropriate protective equipment is potentially hazardous. One worker exposed in a tank for 20 to 45 minutes to a 0.1% to 0.3% solution of ethylene dibromide was intermittently comatose. Death ensued 12 hours later. A co-worker attempted to rescue the first individual and was in the tank for 20 to 30 minutes. He died 64 hours later (Letz et al, 1984). Extensive dermal exposure to the liquid in the tank also occurred. No respiratory or dermal protection was used by either individual. Key effects included coma, metabolic acidosis, acute renal and hepatic failure, and necrosis of skeletal muscle and other organs, as determined postmortem. Evaluation of the liquid contained in the tank and air concentrations of vapors was done two hours after the accident. The tank contained approximately 7.5 centimeters of liquid, comprised of 0.1% to 0.3% of ethylene dibromide, as well as, traces of dichloropropene, dichloropropane, and high concentrations of nitrates and phosphates. The only airborne toxicant detected by gas chromatography was ethylene dibromide, with a range of 15 to 41 ppm. The oxygen level in the tank was 21%. The air was sampled 20 hours after the accident. It is not known if there was any attempt to ventilate the tank during rescue procedures.
Another worker exposed for 30 minutes to high airborne ethylene dibromide concentrations in a confined space became comatose approximately 24 hours after exposure and died within 4 days (Nouchi, 1984). Dermal exposure to liquid ethylene dibromide may have contributed to the dose absorbed and the toxic effects. Marmetschke (1910) and reviewed by Letz et al (1984) reported a death resulting from the accidental use of 22 grams of ethylene dibromide as an anesthetic, administered in a gauze mask. Anesthesia did not occur and the patient died from uterine hemorrhage 44 hours after exposure. Post mortem examination showed fatty degeneration of the myocardium and liver, as well as parenchymal degeneration of the kidneys (Marmetschke, 1910).
INGESTION A woman with a history of ethanol abuse died 54 hours after ingesting two Fumisoil capsules which contained a total of 1.0 mL of ethylene dibromide (Olmstead, 1960). Death was due to profound shock, linked to excessive gastrointestinal tract fluid loss and hepatic necrosis. Estimated ingestion of 15 mL of ethylene dibromide was fatal to a male teenager (Yodaiken & Babcock, 1973). Key effects included hypoglycemia, renal and hepatic failure, hematologic disturbances, pulmonary edema, and cardiac arrest. In 6 cases of poisoning following ingestion of one ampule of ethylene dibromide, 2 died (Saraswat et al, 1986). In a case series of 64 intentional ethylene dibromide ingestions, the smallest amount ingested was 1/2 ampule (1.5 mL). Ten (15.62%) of the cases ingested this amount of ethylene dibromide, and 2 (20%) of these cases expired. Overall mortality was 46.15% and 100% with ingestions of 1 ampule and greater than or equal to 1.5 ampules, respectively (Singh et al, 2007).
DERMAL
MAXIMUM TOLERATED EXPOSURE
INHALATION REPORTED NO OBSERVED EFFECT DOSE - Six hour exposure of workers to 0.75 ppm reportedly produced no symptoms (Perry et al, 1994). CAUTION - There is little information regarding maximum tolerated exposure. Estimates are available (McCollister et al, 1956; Sittig, 1991) Perry et al, 1994). These estimates may be based exclusively on laboratory animal data, may have been estimated prior to documented human fatalities, and may not consider the effects of long term and/or repeated exposures.
INGESTION Acute ingestion of a solution containing 6480 mg ethylene dibromide resulted in a non-fatal case of acute renal failure with hyperkalemia and metabolic encephalopathy in a 20-year-old male (Prakash et al, 1999). Acute ingestion of 3 mL of ethylene dibromide (estimated to be greater than 6000 mg) resulted in acute hepatic and renal failure, metabolic acidosis, and coagulopathy in a 16-year-old male (Singh et al, 2000). In a case series of 64 intentional ethylene dibromide ingestions, the maximum amount ingested and associated with survival was 1 ampule (3 mL). Twenty-six (40.62%) of the cases ingested this amount of ethylene dibromide, and 14 (53.85%) of these cases survived (Singh et al, 2007).
- Carcinogenicity Ratings for CAS106-93-4 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Ethylene dibromide 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): B2 ; Listed as: 1,2-Dibromoethane 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): 2A ; Listed as: Ethylene dibromide 2A : The agent (mixture) is probably carcinogenic to humans. The exposure circumstance entails exposures that are probably carcinogenic to humans. This category is used when there is limited evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals. In some cases, an agent (mixture) may be classified in this category when there is inadequate evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals and strong evidence that the carcinogenesis is mediated by a mechanism that also operates in humans. Exceptionally, an agent, mixture or exposure circumstance may be classified in this category solely on the basis of limited evidence of carcinogenicity in humans.
NIOSH (National Institute for Occupational Safety and Health, 2007): Ca ; Listed as: Ethylene dibromide MAK (DFG, 2002): Category 2 ; Listed as: 1,2-Dibromoethane NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): R ; Listed as: 1,2-Dibromoethane (Ethylene dibromide)
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS106-93-4 (U.S. Environmental Protection Agency, 2011):
Oral: Inhalation: Drinking Water:
References: Clayton & Clayton, 1994 HSDB, 1999 ITI, 1995 Lewis, 1996 RTECS, 2002 LC- (INHALATION)RABBIT: LC50- (INHALATION)GUINEA_PIG: LC50- (INHALATION)RAT: 689 ppm for 1H 14,300 mg/m(3) for 30M
LCLo- (INHALATION)GUINEA_PIG: LD50- (ORAL)CHICKEN: LD50- (ORAL)GUINEA_PIG: LD50- (INTRAPERITONEAL)MOUSE: LD50- (ORAL)MOUSE: 250 mg/kg female, 420 mg/kg
LD50- (ORAL)RABBIT: LD50- (SKIN)RABBIT: LD50- (ORAL)RAT: 108 mg/kg 140 mg/kg 146 mg/kg male, 148 mg/kg female, 117 mg/kg
LD50- (SKIN)RAT: LDLo- (ORAL)HUMAN: LDLo- (ORAL)MOUSE: LDLo- (ORAL)RABBIT: LDLo- (RECTAL)RABBIT: TCLo- (INHALATION)HUMAN: TCLo- (INHALATION)MOUSE: Female, 32 ppm for 23H -- 6-15D of pregnancy Female, 38 ppm for 23H -- 6-15D of pregnancy Female, 20 ppm for 23H -- 6-15D of pregnancy 40 ppm for 6H/90W-I -- CAR
TCLo- (INHALATION)RAT: Female, 66,670 ppb for 4H -- 3-20D of pregnancy Female, 39 ppm for 7H -- 3W prior to mating Female, 80 ppm for 7H -- 3W prior to mating Male, 89 ppm for 7H -- 10W prior to mating Female, 80 ppm for 23H -- 6-15D of pregnancy 10 ppm for 6H; 2Y-I -- CAR
TD- (ORAL)MOUSE: 23 g/kg for 53W-I -- CAR 28 g/kg for 53W-I -- CAR
TD- (ORAL)RAT: TDLo- (ORAL)CATTLE: TDLo- (SUBCUTANEOUS)CATTLE: TDLo- (ORAL)HUMAN: TDLo- (INTRAPERITONEAL)MOUSE: TDLo- (ORAL)MOUSE: TDLo- (SKIN)MOUSE: TDLo- (SUBCUTANEOUS)RABBIT: TDLo- (ORAL)RAT:
CALCULATIONS
1 ppm = 7.86 mg/m(3) (at 25 degrees C; 760 mmHg) (Clayton & Clayton, 1994) 1 ppm = 7.69 mg/m(3) (at 68 degrees F and 760 mmHg) (NIOSH , 1999) 1 mg/L = 130 ppm (Clayton & Clayton, 1994)
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS106-93-4 (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 CAS106-93-4 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS106-93-4 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS106-93-4 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
Listed as: Ethylene dibromide Table Z-1 for Ethylene dibromide: 8-hour TWA: ppm: mg/m3: Ceiling Value: Skin Designation: No Notation(s): Not Listed
Table Z-2 for Ethylene dibromide (Z37.31-1970):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS106-93-4 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS106-93-4 (U.S. Environmental Protection Agency, 2010):
Listed as: Dibromoethane Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Ethane, 1,2-dibromo- Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Ethylene dibromide Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS106-93-4 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS106-93-4 (U.S. Environmental Protection Agency, 2010b):
Listed as: Ethane, 1,2-dibromo- P or U series number: U067 Footnote: Listed as: Ethylene dibromide P or U series number: U067 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 CAS106-93-4 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS106-93-4 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: 1,2-Dibromoethane (Ethylene dibromide) Effective Date for Reporting Under 40 CFR 372.30: 1/1/87 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS106-93-4 (49 CFR 172.101 - App. B, 2005):
Listed as Methyl bromide and ethylene dibromide mixtures, liquid Severe Marine Pollutant: No Listed as Ethylene dibromide and methyl bromide mixtures, liquid Severe Marine Pollutant: No
- EPA TSCA Inventory for CAS106-93-4 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 1605 (49 CFR 172.101, 2005):
- ICAO International Shipping Name for UN1605 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS106-93-4 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
Ethylene dibromide should be stored in a cool, dry, dark, well-ventilated area and away from oxidizing materials, alkali metals, and ammonia (NFPA, 1997). This compound should be protected from light (Budavari, 1996).
STORAGE
Containers of ethylene dibromide should be stored in a cool, dry, dark, well-ventilated area. Containers should be kept away from oxidizing materials, alkali metals, and ammonia (NFPA, 1997). Usual shipping containers include glass bottles; metal cans, pails, drums; and tanks on trucks, rail cars, and barges (NFPA, 1997). This compound should not be shipped with foods, feed, or clothing (HSDB , 1999).
- ROOM/CABINET RECOMMENDATIONS
Storage area should be cool, dry, dark, and well-ventilated (NFPA, 1997).
Ethylene dibromide "may poison platinum catalysts" (Lewis, 1993). Ethylene dibromide may react with chemically active metals, alkali metals, liquid ammonia, sodium, potassium, calcium, powdered aluminum, hot aluminum, zinc, magnesium, liquid ammonia as well as strong oxidizers (NFPA, 1997; NIOSH , 1999; Pohanish & Greene, 1997; Sittig, 1991). Slow decomposition may occur in the presence of heat and light. Compound may attack some plastics and rubber (Pohanish & Greene, 1997). Ethylene dibromide and powdered metals may produce a violent interaction and result in air-sensitive Grignard compounds (Urben, 1995).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (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.
- Persons should wear appropriate protective clothing to prevent prolonged or repeated skin exposure. Appropriate eye protection should also be used. Personnel should immediately wash contaminated skin and remove contaminated clothing. Emergency showers and eyewash fountains should be provided where the potential for exposure exists (NIOSH , 1999; Sittig, 1991). Personnel should avoid breathing vapors or dusts (AAR, 1996).
- Leather foot protection is easily permeated by ethylene dibromide to form dibromoethane and should be discarded if it has been contaminated (HSDB , 1999).
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 106-93-4.
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004) Non-combustible, substance itself does not burn but may decompose upon heating to produce corrosive and/or toxic fumes. Some are oxidizers and may ignite combustibles (wood, paper, oil, clothing, etc.). Contact with metals may evolve flammable hydrogen gas. Containers may explode when heated.
Ethylene dibromide is non-flammable (Lewis, 1998). This compound does not burn, or burns with difficulty (AAR, 1996). Fires involving this compound should be extinguished using an agent suitable for the surrounding fire. Fire-exposed containers can be kept cool using water (NFPA, 1997). Decomposition gases may be toxic and irritating (CHRIS , 1999).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS106-93-4 (NFPA, 2002):
- INITIATING OR CONTRIBUTING PROPERTIES
Ethylene dibromide, when heated to decomposition, emits toxic fumes of hydrogen bromide (Lewis, 1996). Ethylene dibromide may react with chemically active metals, liquid ammonia, strong oxidizers. Slow decomposition may occur in the presence of heat and light. May attack some plastics and rubber (Pohanish & Greene, 1997).
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004)
Dry chemical, CO2, alcohol-resistant foam or water spray. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire.
- NFPA Extinguishing Methods for CAS106-93-4 (NFPA, 2002):
- Ethylene dibromide is non-flammable. Fires involving this compound should be extinguished using an agent suitable for the surrounding fire (Sittig, 1991). Fire-exposed containers can be kept cool with water (NFPA, 1997).
EXPLOSION HAZARD
- Mixtures of liquid ammonia and ethylene dibromide allowed to reach room temperature may result in an explosion with formation of ethylene diamine and higher homologs (HSDB , 1999).
DUST/VAPOR HAZARD
- When heated to decomposition, ethylene dibromide emits toxic fumes of hydrogen bromide (Lewis, 1996).
- Vapors of ethylene dibromide are poisonous if inhaled and are irritating to eyes, nose and throat (CHRIS , 1999).
REACTIVITY HAZARD
- Ethylene dibromide "may poison platinum catalysts" and may attack some plastics and rubber (Lewis, 1993; Pohanish & Greene, 1997). Slow decomposition may occur in the presence of heat and light (Pohanish & Greene, 1997).
- Ethylene dibromide, when heated to decomposition, emits toxic fumes of hydrogen bromide (Lewis, 1996). Ethylene dibromide may react with chemically active metals, liquid ammonia, strong oxidizers (Pohanish & Greene, 1997).
- Ethylene dibromide undergoes vigorous reaction with metals (such as aluminum, magnesium, sodium and potassium), strong alkalis and oxidizing agents (ITI, 1995).
EVACUATION PROCEDURES
- Initial Isolation and Protective Action Distances (ERG, 2004)
Data presented from the Emergency Response Guidebook Table of Initial Isolation and Protective Action Distances are for use when a spill has occurred and there is no fire. If there is a fire, or if a fire is involved, evacuation information presented under FIRE - PUBLIC SAFETY EVACUATION DISTANCES should be used. Generally, a small spill is one that involves a single, small package such as a drum containing up to approximately 200 liters, a small cylinder, or a small leak from a large package. A large spill is one that involves a spill from a large package, or multiple spills from many small packages. Suggested distances to protect from vapors of toxic-by-inhalation and/or water-reactive materials during the first 30 minutes following the spill.
- SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (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 154 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate enclosed areas.
- AIHA ERPG Values for CAS106-93-4 (AIHA, 2006):
- DOE TEEL Values for CAS106-93-4 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS106-93-4 (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):
Listed as: 1,2-Dibromoethane Proposed Value: AEGL-1 10 min exposure: ppm: 52 ppm mg/m3: 400 mg/m(3)
30 min exposure: ppm: 26 ppm mg/m3: 200 mg/m(3)
1 hr exposure: ppm: 17 ppm mg/m3: 131 mg/m(3)
4 hr exposure: ppm: 7.1 ppm mg/m3: 55 mg/m(3)
8 hr exposure: ppm: 4.6 ppm mg/m3: 35 mg/m(3)
Definitions: AEGL-1 is the airborne concentration of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic non-sensory effects. However, the effects are not disabling, are transient, and are reversible upon cessation of exposure.
Listed as: 1,2-Dibromoethane Proposed Value: AEGL-2 10 min exposure: ppm: 73 ppm mg/m3: 562 mg/m(3)
30 min exposure: ppm: 37 ppm mg/m3: 285 mg/m(3)
1 hr exposure: ppm: 24 ppm mg/m3: 185 mg/m(3)
4 hr exposure: ppm: 10 ppm mg/m3: 77 mg/m(3)
8 hr exposure: ppm: 6.5 ppm mg/m3: 50 mg/m(3)
Definitions: AEGL-2 is the airborne concentration 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.
Listed as: 1,2-Dibromoethane Proposed Value: AEGL-3 10 min exposure: ppm: 170 ppm mg/m3: 1308 mg/m(3)
30 min exposure: ppm: 76 ppm mg/m3: 585 mg/m(3)
1 hr exposure: ppm: 46 ppm mg/m3: 354 mg/m(3)
4 hr exposure: ppm: 17 ppm mg/m3: 131 mg/m(3)
8 hr exposure: ppm: 10 ppm mg/m3: 77 mg/m(3)
Definitions: AEGL-3 is the airborne concentration of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening health effects or death.
- NIOSH IDLH Values for CAS106-93-4 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 154 (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.
Spill area should be evacuated (Sittig, 1991). Leaks should be stopped or controlled, only if possible without undue risk (NFPA, 1997). Protective clothing and equipment should be used when handling spilled ethylene dibromide. Area should be ventilated (Sittig, 1991). Foam may be used to blanket the released material and suppress the vapors (NFPA, 1997). Spills may be absorbed using a non-reactive material and shoveled into a safe container for proper disposal (Sittig, 1991). Ethylene dibromide should be kept out of water sources and sewers. Dikes may be used to control flow (AAR, 1996). If ethylene dibromide is spilled on land, pits, ponds, lagoons, or other holding areas may be used to contain the spilled material. Surface flow may be diked using soil, sand bags, foamed polyurethane, or foamed concrete. Bulk liquid may be absorbed with fly ash or cement powder. A universal gelling agent may also be used to immobilize the spill (AAR, 1996). If ethylene dibromide is spilled in a water source, natural deep water pockets, excavated lagoons, or sand bag barriers may be used to trap the spilled material at the bottom of the water source. If ethylene dibromide is dissolved, in a region of 10ppm or greater concentration, activated carbon, at ten times the spilled amount, may be applied. Trapped material may be removed using suction hoses. Mechanical dredges or lifts may be used to remove the immobilized masses of pollutants and precipitates (AAR, 1996). This compound is very harmful to aquatic live in very low concentrations (CHRIS , 1999). ITI (1995) indicates that spilled material may be absorbed with paper towels or similar material and placed in a hood to evaporate. Paper towel may then be burned. Also, waste may be dissolved in a combustible solvent and the solution scattered into a furnace equipped with an afterburner and an alkali scrubber.
Ethylene dibromide may be incinerated using an incinerator equipped with a scrubber and ash disposal (Sittig, 1991). 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
- Ethylene dibromide can enter the environment through its use as a lead scavenger in leaded gasolines and through its use as a fumigant for soil, citrus, grain, fruits, vegetables, tobacco, and seeds. It may also enter the environment through wastewater and emissions from its use as a solvent for resins, gums, and waxes, and through its use as a chemical intermediate in dye and pharmaceutical synthesis (Howard, 1997). HSDB (1999) reports that ethylene dibromide may occur naturally in the ocean waters and air as a result of macro algae growth.
ENVIRONMENTAL FATE AND KINETICS
Ethylene dibromide released into the atmosphere is expected to degrade through its reaction with photochemically produced hydroxyl radicals (half-life of 67 days). This compound may also undergo physical removal through precipitation and dissolution in clouds (Howard, 1997). Half-lives ranging from 10.7 to 107 days have been reported (Howard, 1991).
SURFACE WATER In water, the primary removal process for this compound is evaporation. In a typical river it is expected to have a half-life of just over a day and 5 days in a lake. Sediment adsorption is not expected to be significant. Under anaerobic conditions, ethylene dibromide will not degrade. This compound is persistent in aquifers (Howard, 1997). Surface water half-lives ranging from 4 weeks to 6 months have been reported (Howard, 1991). Groundwater half-lives ranging from 19.6 days to 120 days have been reported (Howard, 1991).
TERRESTRIAL In soil, ethylene dibromide is expected to partially evaporate. Entrapment of this compound in soil micropores is likely; it has been detected in agricultural top soils up to 19 years after the last known application. Freshly administered ethylene dibromide will degrade with half-lives of 4-8 days, while the original compound will not degrade. Ethylene dibromide also has a low sorption to soil and data indicate that it will leach into the soil and penetrate groundwater. In aquifer samples, half-lives of 75 and 50 days under aerobic and anaerobic conditions have been reported. This compound will also not be taken-up by plants (Howard, 1997). Half-lives ranging from 4 weeks to 6 months have been reported (Howard, 1991). Low to moderate soil adsorption was measured for ethylene dibromide. Koc values ranged from 14 to 160 (Howard, 1997).
ABIOTIC DEGRADATION
- Ethylene dibromide is stable toward hydrolysis with reported half-lives ranging from 13.2 years (at pH 7 and 20 degrees C), 8 years (at pH 7 and 20 degrees C), and 2.5 years (at pH 7.5 and 25 degrees C) (Howard, 1997).
BIODEGRADATION
- Aerobic half lives ranging from 4 weeks to 6 months have been reported (Howard, 1991). Anaerobic half-lives ranging from 2 days to 15 days have been reported (Howard, 1991).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- FRESHWATER TOXICITY (CHRIS , 1999; HSDB , 1999)
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Ethylene dibromide exists as a colorless, heavy liquid with a sweet, pleasant, chloroform-like odor (Ashford, 1994; (Lewis, 1996).
- Below 50 degrees F, ethylene dibromide exists as a solid (HSDB , 2002).
- Ethylene dibromide is heavier than water (AAR, 1996).
- This extremely toxic compound slowly decomposes in light (ITI, 1995; Lewis, 1998).
- This compound has low flammability in air (Clayton & Clayton, 1994).
VAPOR PRESSURE
- 17.4 mmHg (at 30 degrees C) (Lewis, 1996)
- 12 mmHg (at 25 degrees C) (Clayton & Clayton, 1994)
- 11.2 mmHg (at 25 degrees C) (Howard, 1997)
- 11.0 mmHg (at 25 degrees C) (Budavari, 1996)
- 1.13 kPa (8.5 mmHg) (at 20 degrees C) (HSDB , 2002)
- 15.98 kPa (119.8 mmHg) (at 75 degrees C) (HSDB , 2002)
- 285.2 mmHg (at 100 degrees C) (HSDB , 2002)
SPECIFIC GRAVITY
- NORMAL TEMPERATURE AND PRESSURE
(25 degrees C; 77 degrees F and 760 mmHg) 2.172 (at 25/25 degrees C) (Budavari, 1996) 2.1701 (at 25/4 degrees C) (Clayton & Clayton, 1994) 2.17 (at 25/4 degrees C) (NIOSH , 1999)
- TEMPERATURE AND/OR PRESSURE NOT LISTED
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
2.17 kg/L (at 20 degrees C) (Ashford, 1994) 2.178 kg/L (at 20/4 degrees C ) (Lewis, 1996) 2.17-2.18 kg/L (at 20 degrees C) (Lewis, 1993)
FREEZING/MELTING POINT
10 degrees C (Ashford, 1994) 9.3 degrees C (Lewis, 1996) 9 degrees C (Budavari, 1996) 50 degrees F (CHRIS , 1999) 9.8 degrees C; 49.6 degrees F; 283.0 degrees K (CHRIS , 1999)
10 degrees C; 50 degrees F (Lewis, 1996; NFPA, 1997) 9.97 degrees C (ACGIH, 1991; Clayton & Clayton, 1994) 9.8 degrees C (Howard, 1997) 9.1 degrees C (ITI, 1995)
BOILING POINT
- 131 degrees C; 268 degrees F; 404 degrees K (Ashford, 1994; (CHRIS , 1999; Lewis, 1993; Sittig, 1991)
- 131.4 degrees C (Lewis, 1996)
- 131.6 degrees C (Clayton & Clayton, 1994)
- 131-132 degrees C; 268-270 degrees F (Budavari, 1996; NFPA, 1997)
- 132 degrees C (ACGIH, 1991)
FLASH POINT
EXPLOSIVE LIMITS
SOLUBILITY
Ethylene dibromide is insoluble in water (Ashford, 1994; (NFPA, 1997) Soluble in about 250 parts water (Budavari, 1996) Emulsifiable (Lewis, 1993) Slightly soluble in water (0.43 g/100 mL) (at 30 degrees C) (AAR, 1996; (ACGIH, 1991; Clayton & Clayton, 1994) 4150 mg/L (at 25 degrees C) (Howard, 1997) 0.34 g/100 mL (at 20 degrees C) (HSDB , 2002) 0.404 g/100 mL (at 20 degrees C) (HSDB , 2002)
Ethylene dibromide is soluble in oxygenated solvents (Ashford, 1994). Miscible with alcohol and ether (Budavari, 1996). Miscible with most solvents and thinners (Lewis, 1998). Soluble in ethanol, ether, and most organic solvents (ACGIH, 1991)
OCTANOL/WATER PARTITION COEFFICIENT
- Log Kow=1.96 (Howard, 1997)
HENRY'S CONSTANT
- 6.67x10(-4) atm-m(3) (at 25 degrees C) (calculated) (Howard, 1997)
SPECTRAL CONSTANTS
OTHER/PHYSICAL
10 ppm (Sittig, 1991) Low: 76.80 mg/m(3) (HSDB , 2002) High: 62.5 mg/m(3) (HSDB , 2002)
- ORGANIC CARBON PARTITION COEFFICIENT
1.5379 (at 20 degrees C) (Budavari, 1996) 1.53789 (at 20 degrees C) (Clayton & Clayton, 1994) 1.5337 (at 25 degrees C) (Lewis, 1993)
- LIQUID WATER INTERFACIAL TENSION
- NUCLEAR MAGNETIC RESONANCE
-REFERENCES
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