TABUN
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
AGENT GA DIMETHYLAMIDOETHOXYPHOSPHORYL CYANIDE DIMETHYLAMINOETHODYCYANOPHOSPHINE OXIDE DIMETHYLAMINOCYANPHOSPHORSAEUREAETHYLESTER (German) DIMETHYLPHOSPHORAMIDOCYANIDIC ACID, ETHYL ESTER EA 1205 ETHYL DIMETHYLAMIDOCYANOPHOSPHATE ETHYL DIMETHYLPHOSPHORAMIDOCYANIDATE ETHYL N-DIMETHYLPHOSPHORAMIDOCYANIDATE ETHYL N,N-DIMETHYLPHOSPHORAMIDOCYANIDATE ETHYL N,N-DIMETHYLAMINO CYANOPHOSPHATE ETHYLESTER-DIMETHYLAMID KYSELINY KYANFOSFONOVE (Czech) ETHYL-N,N-DIMETHYLPHOSPHORAMIDOCYANIDATE ETHYL PHOSPHORODIMETHYLAMIDOCYANIDATE GA GELAN I Le-100 MCE O-ETHYL N,N-DIMETHYLPHOSPHORAMIDOCYANIDATE PHOSPHORAMIDOCYANIDIC ACID, DIMETHYL-, ETHYL ESTER T-2104 TL 1578 TABOON A TABUN TRILON 83
IDENTIFIERS
SYNONYM REFERENCE
- (EPA, 1985; HSDB , 2001; Lewis, 1998; Lewis, 2000; RTECS , 2001)
USES/FORMS/SOURCES
Tabun is a liquid with a fruity smell that gives off a colorless vapor (SBCCOM , 2001; Munro et al, 1999a). Tabun is seldom found in its pure form and usually contains a thickener. The contaminants are usually degradation products and production by-products (Munro et al, 1999a).
Tabun was discovered by the Germans in 1937, and was the first nerve agent in large scale production. It was produced and stockpiled beginning in 1942, but only small quantities were produced in the United States. Nonstockpile locations that house tabun are Tooele Army Depot, Utah; Edgewood Arsenal, Maryland, Dugway Proving Ground, Utah; and the Virgin Islands (Munro et al, 1999a). Tabun is manufactured, in the presence of ethanol, from dimethylamidophosphoryl dichloride and sodium cyanide (Budavari, 2000).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Tabun is a nerve gas. It is a typical cholinesterase inhibitor with an especially rapid onset of action, which on a weight basis is less potent than VX. It can be hazardous by any route of exposure. It generates CYANOGEN CHLORIDE upon decontamination with bleach, and HYDROGEN CYANIDE upon contact with water or acids.
- The following are symptoms from organophosphates in general, which are due to the anticholinesterase activity of this class of compounds. All of these effects may not be documented for tabun, but could potentially occur in individual cases.
- MUSCARINIC (PARASYMPATHETIC) EFFECTS may include bradycardia, bronchospasm, bronchorrhea, salivation, lacrimation, diaphoresis, vomiting, diarrhea, and miosis.
- NICOTINIC (SYMPATHETIC AND MOTOR) EFFECTS may include tachycardia, hypertension, fasciculations, muscle cramps, weakness, and RESPIRATORY PARALYSIS.
- CENTRAL EFFECTS may include CNS depression, agitation, confusion, psychosis, delirium, coma, and seizures.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
TOXIC; inhalation, ingestion or skin contact with material may cause severe injury or death. Contact with molten substance may cause severe burns to skin and eyes. Avoid any skin contact. Effects of contact or inhalation may be delayed. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
ACUTE CLINICAL EFFECTS
- Based on its acute oral LD50 of 3.7 mg/kg in rats (RTECS , 1993), tabun is a HIGHLY TOXIC organophosphate compound (Morgan, 1989). The human fatal dose of tabun has been said to be 0.01 mg/kg (Sax & Lewis, 1987; Sittig, 1985; EPA, 1985).
- The median lethal tabun dose by inhalation for humans is 400 mg/minute/m(3), and is fatal in 1 to 10 minutes; the median incapacitating tabun dose by inhalation in humans is 300 mg/minute/m(3) (HSDB , 1993).
- Tabun is particularly toxic following inhalational exposure (Sax & Lewis, 1987), but can be absorbed following ingestion or dermal or eye contact (Sax & Lewis, 1989; Budavari, 1989; EPA, 1985). Tabun vapor does not readily penetrate intact skin, but the liquid is rapidly absorbed following dermal contact (Sax & Lewis, 1989). Sufficient tabun can be absorbed through the skin to cause death; this may occur as soon as 1 to 2 minutes after exposure, or it can be delayed for 1 to 2 hours (EPA, 1985).
- The hallmark of organophosphate poisoning is inhibition of plasma pseudocholinesterase and erythrocyte acetylcholinesterase (Namba, 1972).
- Effects of organophosphate poisoning include nausea, vomiting, abdominal cramps, diarrhea, headache, giddiness, vertigo, weakness, sensation of tightness in the chest (after inhalation exposures), excessive tearing, loss of accommodation, ocular pain, blurring or dimness of vision, miosis, loss of muscle coordination, slurring of speech, fasciculations and twitching of muscles (particularly of tongue and eyelids), generalized profound weakness, mental confusion, disorientation, drowsiness, difficulty in breathing, excessive salivation and respiratory mucus, oronasal frothing, cyanosis, pulmonary rales and rhonchi, hypertension, hypotension, cardiac arrhythmias, random jerking movements, incontinence, convulsions, and coma (AH Hall , 1993).
- Death from organophosphate poisoning occurs primarily from respiratory arrest arising from failure of the respiratory center, paralysis of respiratory muscles, intense bronchoconstriction, or all three (HSDB , 1993). In severe cases when the patient has been unconscious for some time, brain damage can occur from lack of oxygen (ILO, 1983). Experimental animal studies suggest that brain damage from nerve agents may result from inadequate oxygenation of the brain, prolonged and excessively increased neuronal activity, and/or direct neurotoxic effects of the nerve agent (Somani, 1992; Sidell, 1992). Neuronal degeneration and behavioral deficits in performance have been reported in animals which survived acute intoxication by Soman or VX nerve agents (Sidell, 1992).
- Some effects of acute organophosphate poisoning, based upon experience with parathion, can persist for days to months. These include fatigue, ocular symptoms, EEG abnormalities, gastrointestinal complaints, excessive dreams, and intolerance to exposure to organophosphates (ILO, 1983).
- Delayed effects may be most pronounced with highly lipid-soluble organophosphates, such as fenthion, or the phosphorothioates, such as chlorpyrifos. After an initial period of apparent recovery, clinical effects may reoccur for up to several weeks after an acute exposure (Minton & Murray, 1988).
- Some organophosphates can induce delayed neurological effects of a motor or combined sensory-motor peripheral polyneuropathy. Sensation of numbness or tingling in the extremities may appear several weeks after acute exposure. It is not clear if all organophosphates have this activity (Cherniack, 1986; Wadia et al, 1987). Tabun did not induce delayed neuropathy in hens (Willems et al, 1984; Henderson et al, 1992).
- Tabun induced a 4- to 6-degree drop in body temperature in rats (Meeter & Wolthuis, 1968). In cats, the primary cause for respiratory arrest in tabun poisoning was found to be loss of the central respiratory drive (Rickett et al, 1986).
CHRONIC CLINICAL EFFECTS
- At the time of this review, no studies were found on chronic tabun exposure in humans.
- In general, chronic exposure to organophosphates can lead to cumulative depression of cholinesterase levels until a critical lack of activity causes symptoms of organophosphate poisoning to appear, in a pattern similar to that of acute poisoning (Coye et al, 1986). The level of chronic exposure which can be tolerated depends on the rate of uptake and degradation of the organophosphate in the body in relation to its potency in inhibiting acetylcholinesterase, and the rate of the individual's replenishment of acetylcholinesterase activity.
- Rats treated with a dose of 100 mcg/kg of tabun daily for 85 days had reduced growth rates that required 38 days to return to normal following cessation of exposure (Dulaney et al, 1985). In striated muscle, the acetylcholinesterase activity in treated animals was only 13% of control (Dulaney et al, 1985).
- Tabun did not induced delayed neurotoxicity in the standard hen assay after administration 5 times per week for 90 days (Henderson et al, 1993). Studies in hens have reported that tabun inhibits the enzyme neurotoxic esterase, an effect associated with delayed neuropathy (Somani, 1992).
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance; give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
GENERAL The following information is for Organophosphate Compounds in general. Severe toxicity may develop rapidly following exposure or may be delayed by 12 hours or more. Rapid removal from toxic environments, decontamination procedures, and specific therapy if required are essential. First responders, emergency medical, and emergency department personnel should take proper precautions (wear rubber gowns, rubber aprons, rubber gloves, etc) when treating patients with organophosphate poisoning to avoid contamination. Emesis containing organophosphates should be placed in closed impervious containers for proper disposal.
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 respiratory tract irritation or respiratory depression is evident, monitor arterial blood gases, chest x-ray, and pulmonary function tests. Carefully observe patients with inhalation exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
DERMAL EXPOSURE Systemic effects can occur from dermal exposure to organophosphates. 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). Some chemicals can produce systemic poisoning by absorption through intact skin. Carefully observe patients with dermal exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
EYE EXPOSURE DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility. Patients symptomatic following exposure should be observed in a controlled setting until all signs and symptoms have fully resolved.
ORAL/PARENTERAL EXPOSURE Inducing emesis is contraindicated because of possible early onset of respiratory depression and seizures. PREHOSPITAL ACTIVATED CHARCOAL ADMINISTRATION Consider prehospital administration of activated charcoal as an aqueous slurry in patients with a potentially toxic ingestion who are awake and able to protect their airway. Activated charcoal is most effective when administered within one hour of ingestion. Administration in the prehospital setting has the potential to significantly decrease the time from toxin ingestion to activated charcoal administration, although it has not been shown to affect outcome (Alaspaa et al, 2005; Thakore & Murphy, 2002; Spiller & Rogers, 2002). In patients who are at risk for the abrupt onset of seizures or mental status depression, activated charcoal should not be administered in the prehospital setting, due to the risk of aspiration in the event of spontaneous emesis. The addition of flavoring agents (cola drinks, chocolate milk, cherry syrup) to activated charcoal improves the palatability for children and may facilitate successful administration (Guenther Skokan et al, 2001; Dagnone et al, 2002).
ACTIVATED CHARCOAL: Administer charcoal as a slurry (240 mL water/30 g charcoal). Usual dose: 25 to 100 g in adults/adolescents, 25 to 50 g in children (1 to 12 years), and 1 g/kg in infants less than 1 year old. Suction oral secretions. ANTIDOTES 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.
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. HYPOTENSION: Infuse 10 to 20 mL/kg isotonic fluid. If hypotension persists, administer dopamine (5 to 20 mcg/kg/min) or norepinephrine (ADULT: begin infusion at 0.5 to 1 mcg/min; CHILD: begin infusion at 0.1 mcg/kg/min); titrate to desired response. CONTRAINDICATIONS: Succinylcholine and other cholinergic agents are contraindicated.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
The lethal dose for humans may be as low as 0.01 mg/kg (HSDB , 2001; Lewis, 1997; Sittig, 1991). 400 mg-minute/m(3) is the median respiratory lethal dose for humans. Lethal dosages can kill in 1 to 10 minutes (Sittig, 1991). The lowest published lethal dose for humans is 14 mcg/kg by intravenous route (RTECS , 2001). The lowest published lethal respiratory concentration for humans is 150 mg/m(3) (RTECS , 2001).
MAXIMUM TOLERATED EXPOSURE
To date, OSHA has not promulgated permissible exposure concentrations for tabun (SBCCOM, 1999). Tabun is not listed by the International Agency for Research on Cancer, American Conference of Governmental Industrial Hygienists, Occupational Safety and Health Administration, or National Toxicology Program as a carcinogen (SBCCOM, 1999).
- Carcinogenicity Ratings for CAS77-81-6 :
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 CAS77-81-6 (U.S. Environmental Protection Agency, 2011):
References: HSDB, 2001 ITI, 1995 Lewis, 2000 RTECS, 2001 LC50- (INHALATION)DOG: LC50- (INHALATION)MOUSE: LC50- (INHALATION)PRIMATE: LCLo- (INHALATION)HUMAN: LD50- (INTRAVENOUS)CAT: LD50- (INTRAMUSCULAR)CHICKEN: LD50- (SUBCUTANEOUS)CHICKEN: LD50- (INTRAVENOUS)DOG: LD50- (ORAL)DOG: LD50- (SKIN)DOG: LD50- (SUBCUTANEOUS)DOG: LD50- (SKIN)GUINEA_PIG: LD50- (SUBCUTANEOUS)GUINEA_PIG: LD50- (SUBCUTANEOUS)HAMSTER: LD50- (INTRAMUSCULAR)MOUSE: LD50- (INTRAPERITONEAL)MOUSE: LD50- (INTRAVENOUS)MOUSE: LD50- (SKIN)MOUSE: LD50- (SUBCUTANEOUS)MOUSE: LD50- (INTRAMUSCULAR)PRIMATE: LD50- (INTRAVENOUS)PRIMATE: LD50- (SKIN)PRIMATE: LD50- (SUBCUTANEOUS)PRIMATE: LD50- (INTRAVENOUS)RABBIT: 63 mcg/kg 66 mcg/kg (Lewis, 2000)
LD50- (ORAL)RABBIT: LD50- (SKIN)RABBIT: LD50- (SUBCUTANEOUS)RABBIT: LD50- (INTRAMUSCULAR)RAT: LD50- (INTRAPERITONEAL)RAT: LD50- (INTRAVENOUS)RAT: LD50- (ORAL)RAT: LD50- (SKIN)RAT: LD50- (SUBCUTANEOUS)RAT: LDLo- (SKIN)DOG: LDLo- (INTRAVENOUS)HUMAN: LDLo- (SKIN)HUMAN: LDLo- (SKIN)RAT: TCLo- (INHALATION)HUMAN: TDLo- (INTRAMUSCULAR)CHICKEN: TDLo- (SUBCUTANEOUS)RAT:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS77-81-6 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS77-81-6 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS77-81-6 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS77-81-6 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS77-81-6 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS77-81-6 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS77-81-6 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS77-81-6 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS77-81-6 (U.S. Environmental Protection Agency, 2010):
Listed as: Tabun Reportable Quantity, in pounds: 10 Threshold Planning Quantity, in pounds: Note(s): b b: The calculated TPQ changed after technical review as described in a technical support document for the final rule, April 22, 1987. d: Revised TPQ based on new or re-evaluated toxicity data, April 22, 1987.
- EPA SARA Title III, Community Right-to-Know for CAS77-81-6 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS77-81-6 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS77-81-6 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions for UN/NA Number 2810 (49 CFR 172.101, 2005):
Hazardous materials descriptions and proper shipping name: Compounds, tree killing, liquid or Compounds, weed killing, liquid Symbol(s): D, G D: identifies proper shipping names which are appropriate for describing materials for domestic transportation but may be inappropriate for international transportation under the provisions of international regulations (e.g., IMO, ICAO). An alternate proper shipping name may be selected when either domestic or international transportation is involved. G: identifies proper shipping names for which one or more technical names of the hazardous material must be entered in parentheses, in association with the basic description. (See 40 CFR 172.203(k).)
Hazard class or Division: 6.1 Identification Number: NA2810 Packing Group: I Label(s) required (if not excepted): 6.1 Special Provisions: T14, TP2, TP13, TP27 T14: Minimum test pressure (bar): 6; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): 6 mm; Pressure-relief requirements (See sxn.178.275(g)): section 178.275(g)(3); Bottom opening requirements (See sxn.178.275(d)): Prohibited. TP2: a. The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 95/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, tf is the temperature in degrees celsius of the liquid during filling, and alpha is the mean coefficient of cubical expansion of the liquid between the mean temperature of the liquid during filling (tf) and the maximum mean bulk temperature during transportation (tr) both in degrees celsius; and b. For liquids transported under ambient conditions a may be calculated using the formula: [alpha = (d15-d50)/(35 x d50)], where d15 and d50 are the densities (in units of mass per unit volume) of the liquid at 15 degrees C (59 degrees F) and 50 degrees C (122 degrees F), respectively. TP13: Self-contained breathing apparatus must be provided when this hazardous material is transported by sea. TP27: A portable tank having a minimum test pressure of 4 bar (400 kPa) may be used provided the calculated test pressure is 4 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP.
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: None Non-bulk packaging: 201 Bulk packaging: 243
Quantity Limitations: Vessel Stowage Requirements:
Hazardous materials descriptions and proper shipping name: Compounds, tree killing, liquid or Compounds, weed killing, liquid Symbol(s): Not Listed Hazard class or Division: 6.1 Identification Number: NA2810 Packing Group: II Label(s) required (if not excepted): 6.1 Special Provisions: IB2, T11, TP2, TP27 IB2: Authorized IBCs: Metal (31A, 31B and 31N); Rigid plastics (31H1 and 31H2); Composite (31HZ1). Additional Requirement: Only liquids with a vapor pressure less than or equal to 110 kPa at 50 °C (1.1 bar at 122 °F), or 130kPa at 55 °C (1.3 bar at 131 °F) are authorized. T11: Minimum test pressure (bar): 6; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): sxn.178.274(d)(2); Pressure-relief requirements (See sxn.178.275(g)): Normal; Bottom opening requirements (See sxn.178.275(d)): sxn.178.275(d)(3). TP2: a. The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 95/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, tf is the temperature in degrees celsius of the liquid during filling, and alpha is the mean coefficient of cubical expansion of the liquid between the mean temperature of the liquid during filling (tf) and the maximum mean bulk temperature during transportation (tr) both in degrees celsius; and b. For liquids transported under ambient conditions a may be calculated using the formula: [alpha = (d15-d50)/(35 x d50)], where d15 and d50 are the densities (in units of mass per unit volume) of the liquid at 15 degrees C (59 degrees F) and 50 degrees C (122 degrees F), respectively. TP27: A portable tank having a minimum test pressure of 4 bar (400 kPa) may be used provided the calculated test pressure is 4 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP.
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: 153 Non-bulk packaging: 202 Bulk packaging: 243
Quantity Limitations: Vessel Stowage Requirements:
Hazardous materials descriptions and proper shipping name: Compounds, tree killing, liquid or Compounds, weed killing, liquid Symbol(s): Not Listed Hazard class or Division: 6.1 Identification Number: NA2810 Packing Group: III Label(s) required (if not excepted): 6.1 Special Provisions: IB3, T7, TP1, TP28 IB3: Authorized IBCs: Metal (31A, 31B and 31N); Rigid plastics (31H1 and 31H2); Composite (31HZ1 and 31HA2, 31HB2, 31HN2, 31HD2 and 31HH2). Additional Requirement: Only liquids with a vapor pressure less than or equal to 110 kPa at 50 °C (1.1 bar at 122 °F), or 130 kPa at 55 °C (1.3 bar at 131 °F) are authorized, except for UN2672 (also see Special Provision IP8 in Table 3 for UN2672). T7: Minimum test pressure (bar): 4; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): sxn.178.274(d)(2); Pressure-relief requirements (See sxn.178.275(g)): Normal; Bottom opening requirements (See sxn.178.275(d)): sxn.178.275(d)(3). TP1: The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 97/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, and tf is the temperature in degrees celsius of the liquid during filling. TP28: A portable tank having a minimum test pressure of 2.65 bar (265 kPa) may be used provided the calculated test pressure is 2.65 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP.
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: 153 Non-bulk packaging: 203 Bulk packaging: 241
Quantity Limitations: Vessel Stowage Requirements:
Hazardous materials descriptions and proper shipping name: Toxic, liquids, organic, n.o.s Symbol(s): G Hazard class or Division: 6.1 Identification Number: UN2810 Packing Group: I Label(s) required (if not excepted): 6.1 Special Provisions: T14, TP2, TP13, TP27 T14: Minimum test pressure (bar): 6; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): 6 mm; Pressure-relief requirements (See sxn.178.275(g)): section 178.275(g)(3); Bottom opening requirements (See sxn.178.275(d)): Prohibited. TP2: a. The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 95/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, tf is the temperature in degrees celsius of the liquid during filling, and alpha is the mean coefficient of cubical expansion of the liquid between the mean temperature of the liquid during filling (tf) and the maximum mean bulk temperature during transportation (tr) both in degrees celsius; and b. For liquids transported under ambient conditions a may be calculated using the formula: [alpha = (d15-d50)/(35 x d50)], where d15 and d50 are the densities (in units of mass per unit volume) of the liquid at 15 degrees C (59 degrees F) and 50 degrees C (122 degrees F), respectively. TP13: Self-contained breathing apparatus must be provided when this hazardous material is transported by sea. TP27: A portable tank having a minimum test pressure of 4 bar (400 kPa) may be used provided the calculated test pressure is 4 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP.
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: None Non-bulk packaging: 201 Bulk packaging: 243
Quantity Limitations: Vessel Stowage Requirements:
Hazardous materials descriptions and proper shipping name: Toxic, liquids, organic, n.o.s Symbol(s): Not Listed Hazard class or Division: 6.1 Identification Number: UN2810 Packing Group: II Label(s) required (if not excepted): 6.1 Special Provisions: IB2, T11, TP2, TP13, TP27 IB2: Authorized IBCs: Metal (31A, 31B and 31N); Rigid plastics (31H1 and 31H2); Composite (31HZ1). Additional Requirement: Only liquids with a vapor pressure less than or equal to 110 kPa at 50 °C (1.1 bar at 122 °F), or 130kPa at 55 °C (1.3 bar at 131 °F) are authorized. T11: Minimum test pressure (bar): 6; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): sxn.178.274(d)(2); Pressure-relief requirements (See sxn.178.275(g)): Normal; Bottom opening requirements (See sxn.178.275(d)): sxn.178.275(d)(3). TP2: a. The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 95/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, tf is the temperature in degrees celsius of the liquid during filling, and alpha is the mean coefficient of cubical expansion of the liquid between the mean temperature of the liquid during filling (tf) and the maximum mean bulk temperature during transportation (tr) both in degrees celsius; and b. For liquids transported under ambient conditions a may be calculated using the formula: [alpha = (d15-d50)/(35 x d50)], where d15 and d50 are the densities (in units of mass per unit volume) of the liquid at 15 degrees C (59 degrees F) and 50 degrees C (122 degrees F), respectively. TP13: Self-contained breathing apparatus must be provided when this hazardous material is transported by sea. TP27: A portable tank having a minimum test pressure of 4 bar (400 kPa) may be used provided the calculated test pressure is 4 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP.
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: 153 Non-bulk packaging: 202 Bulk packaging: 243
Quantity Limitations: Vessel Stowage Requirements:
Hazardous materials descriptions and proper shipping name: Toxic, liquids, organic, n.o.s Symbol(s): Not Listed Hazard class or Division: 6.1 Identification Number: UN2810 Packing Group: III Label(s) required (if not excepted): 6.1 Special Provisions: IB3, T7, TP1, TP28 IB3: Authorized IBCs: Metal (31A, 31B and 31N); Rigid plastics (31H1 and 31H2); Composite (31HZ1 and 31HA2, 31HB2, 31HN2, 31HD2 and 31HH2). Additional Requirement: Only liquids with a vapor pressure less than or equal to 110 kPa at 50 °C (1.1 bar at 122 °F), or 130 kPa at 55 °C (1.3 bar at 131 °F) are authorized, except for UN2672 (also see Special Provision IP8 in Table 3 for UN2672). T7: Minimum test pressure (bar): 4; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): sxn.178.274(d)(2); Pressure-relief requirements (See sxn.178.275(g)): Normal; Bottom opening requirements (See sxn.178.275(d)): sxn.178.275(d)(3). TP1: The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 97/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, and tf is the temperature in degrees celsius of the liquid during filling. TP28: A portable tank having a minimum test pressure of 2.65 bar (265 kPa) may be used provided the calculated test pressure is 2.65 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP.
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: 153 Non-bulk packaging: 203 Bulk packaging: 241
Quantity Limitations: Vessel Stowage Requirements:
Hazardous materials descriptions and proper shipping name: Toxic, liquids, organic, n.o.s. Inhalation hazard, Packing Group I, Zone A Symbol(s): G Hazard class or Division: 6.1 Identification Number: UN2810 Packing Group: I Label(s) required (if not excepted): 6.1 Special Provisions: 1, B9, B14, B30, B72, T22, TP2, TP13, TP27, TP38, TP44 1: This material is poisonous by inhalation (see sxn. 171.8 of this subchapter) in Hazard Zone A (see sxn. 173.116(a) or sxn. 173.133(a) of this subchapter), and must be described as an inhalation hazard under the provisions of this subchapter. B9: Bottom outlets are not authorized. B14: Each bulk packaging, except a tank car or a multi-unit-tank car tank, must be insulated with an insulating material so that the overall thermal conductance at 15.5 °C (60 °F) is no more than 1.5333 kilojoules per hour per square meter per degree Celsius (0.075 Btu per hour per square foot per degree Fahrenheit) temperature differential. Insulating materials must not promote corrosion to steel when wet. B30: MC 312, MC 330, MC 331 and DOT 412 cargo tanks and DOT 51 portable tanks must be made of stainless steel, except that steel other than stainless steel may be used in accordance with the provisions of sxn. 173.24b(b) of this subchapter. Thickness of stainless steel for tank shell and heads for cargo tanks and portable tanks must be the greater of 7.62 mm (0.300 inch) or the thickness required for a tank with a design pressure at least equal to 1.5 times the vapor pressure of the lading at 46 °C (115 °F). In addition, MC 312 and DOT 412 cargo tank motor vehicles must: a. Be ASME Code (U) stamped for 100% radiography of all pressure-retaining welds; b. Have accident damage protection which conforms with sxn. 178.345-8 of this subchapter; c. Have a MAWP or design pressure of at least 87 psig: and d. Have a bolted manway cover. B72: Tank cars must have a test pressure of 34.47 Bar (500 psig) or greater and conform to Class 105J, 106, or 110. T22: Minimum test pressure (bar): 10; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): 10 mm; Pressure-relief requirements (See sxn.178.275(g)): sxn. 178.275(g)(3); Bottom opening requirements (See sxn.178.275(d)): Prohibited. TP2: a. The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 95/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, tf is the temperature in degrees celsius of the liquid during filling, and alpha is the mean coefficient of cubical expansion of the liquid between the mean temperature of the liquid during filling (tf) and the maximum mean bulk temperature during transportation (tr) both in degrees celsius; and b. For liquids transported under ambient conditions a may be calculated using the formula: [alpha = (d15-d50)/(35 x d50)], where d15 and d50 are the densities (in units of mass per unit volume) of the liquid at 15 degrees C (59 degrees F) and 50 degrees C (122 degrees F), respectively. TP13: Self-contained breathing apparatus must be provided when this hazardous material is transported by sea. TP27: A portable tank having a minimum test pressure of 4 bar (400 kPa) may be used provided the calculated test pressure is 4 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP. TP38: Each portable tank must be insulated with an insulating material so that the overall thermal conductance at 15.5 °C (60 °F) is no more than 1.5333 kilojoules per hour per square meter per degree Celsius (0.075 Btu per hour per square foot per degree Fahrenheit) temperature differential. Insulating materials may not promote corrosion to steel when wet. TP44: Each portable tank must be made of stainless steel, except that steel other than stainless steel may be used in accordance with the provisions of sxn. 173.24b(b) of this subchapter. Thickness of stainless steel for tank shell and heads must be the greater of 7.62 mm (0.300 inch) or the thickness required for a portable tank with a design pressure at least equal to 1.5 times the vapor pressure of the hazardous material at 46 °C (115 °F).
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: None Non-bulk packaging: 226 Bulk packaging: 244
Quantity Limitations: Vessel Stowage Requirements:
Hazardous materials descriptions and proper shipping name: Toxic, liquids, organic, n.o.s. Inhalation hazard, Packing Group I, Zone B Symbol(s): G Hazard class or Division: 6.1 Identification Number: UN2810 Packing Group: I Label(s) required (if not excepted): 6.1 Special Provisions: 2, B9, B14, B32, B74, T20, TP2, TP13, TP27, TP38, TP45 2: This material is poisonous by inhalation (see sxn. 171.8 of this subchapter) in Hazard Zone B (see sxn. 173.116(a) or sxn. 173.133(a) of this subchapter), and must be described as an inhalation hazard under the provisions of this subchapter. B9: Bottom outlets are not authorized. B14: Each bulk packaging, except a tank car or a multi-unit-tank car tank, must be insulated with an insulating material so that the overall thermal conductance at 15.5 °C (60 °F) is no more than 1.5333 kilojoules per hour per square meter per degree Celsius (0.075 Btu per hour per square foot per degree Fahrenheit) temperature differential. Insulating materials must not promote corrosion to steel when wet. B32: MC 312, MC 330, MC 331, DOT 412 cargo tanks and DOT 51 portable tanks must be made of stainless steel, except that steel other than stainless steel may be used in accordance with the provisions of sxn. 173.24b(b) of this subchapter. Thickness of stainless steel for tank shell and heads for cargo tanks and portable tanks must be the greater of 6.35 mm (0.250 inch) or the thickness required for a tank with a design pressure at least equal to 1.3 times the vapor pressure of the lading at 46 °C (115 °F). In addition, MC 312 and DOT 412 cargo tank motor vehicles must: a. Be ASME Code (U) stamped for 100% radiography of all pressure-retaining welds; b. Have accident damage protection which conforms with sxn. 178.345-8 of this subchapter; c. Have a MAWP or design pressure of at least 87 psig; and d. Have a bolted manway cover. B74: Tank cars must have a test pressure of 20.68 Bar (300 psig) or greater and conform to Class 105S, 106, 110, 112J, 114J or 120S. T20: Minimum test pressure (bar): 10; Minimum shell thickness (in mm-reference steel) (See sxn.178.274(d)): 8 mm; Pressure-relief requirements (See sxn.178.275(g)): sxn. 178.275(g)(3); Bottom opening requirements (See sxn.178.275(d)): Prohibited. TP2: a. The maximum degree of filling must not exceed the degree of filling determined by the following: [Degree of filling = 95/1+alpha(tr - tf)], where tr is the maximum mean bulk temperature during transport, tf is the temperature in degrees celsius of the liquid during filling, and alpha is the mean coefficient of cubical expansion of the liquid between the mean temperature of the liquid during filling (tf) and the maximum mean bulk temperature during transportation (tr) both in degrees celsius; and b. For liquids transported under ambient conditions a may be calculated using the formula: [alpha = (d15-d50)/(35 x d50)], where d15 and d50 are the densities (in units of mass per unit volume) of the liquid at 15 degrees C (59 degrees F) and 50 degrees C (122 degrees F), respectively. TP13: Self-contained breathing apparatus must be provided when this hazardous material is transported by sea. TP27: A portable tank having a minimum test pressure of 4 bar (400 kPa) may be used provided the calculated test pressure is 4 bar or less based on the MAWP of the hazardous material, as defined in sxn. 178.275 of this subchapter, where the test pressure is 1.5 times the MAWP. TP38: Each portable tank must be insulated with an insulating material so that the overall thermal conductance at 15.5 °C (60 °F) is no more than 1.5333 kilojoules per hour per square meter per degree Celsius (0.075 Btu per hour per square foot per degree Fahrenheit) temperature differential. Insulating materials may not promote corrosion to steel when wet. TP45: Each portable tank must be made of stainless steel, except that steel other than stainless steel may be used in accordance with the provisions of 173.24b(b) of this subchapter. Thickness of stainless steel for portable tank shells and heads must be the greater of 6.35 mm (0.250 inch) or the thickness required for a portable tank with a design pressure at least equal to 1.3 times the vapor pressure of the hazardous material at 46 °C (115 °F).
Packaging Authorizations (refer to 49 CFR 173.***): Exceptions: None Non-bulk packaging: 227 Bulk packaging: 244
Quantity Limitations: Vessel Stowage Requirements:
- ICAO International Shipping Name for UN2810 (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS77-81-6 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
Use the buddy system when handling chemical agents. No smoking, eating, or drinking is permitted in areas where the chemical is present (SBCCOM, 1999). "Locations where chemical agents and munitions are stored, handled, used, and processed require the use of chemical hazard symbols. These symbols shall be used by themselves or in conjunction with fire symbols as appropriate" (U.S. Army, 1997). "When equipment, tools, or others items or materials come into contact with liquid agent they will be marked, tagged or segregated to indicate the degree of contamination." (U.S. Army, 1997). For additional information refer to AR 385-61, the "Army Toxic Chemical Agent Safety Program," and DA Pam 385-61, "Toxic Chemical Agent Safety Standards" (SBCCOM, 1999).
HANDLING
- Decontamination equipment should be readily located and marked (SBCCOM, 1999).
- Hands should be washed before meals. Personnel should shower thoroughly with special attention to hair, face, neck, and hands using plenty of soap and water before leaving at the end of the work day (SBCCOM, 1999).
STORAGE
Tabun has been stored in heavy steel ton containers, mortar projectiles, rockets, artillery shells, and land mines (USACHPPM , 2001). Tabun will remain stable in steel containers for several years (SBCCOM, 1999). Containers should be inspected periodically (visual or detector kit inspection) (SBCCOM, 1999). Ton containers should be kept painted and free from rust to enhance visual detection of leakage at the valves and plugs. Some agents (Mustard, Lewisite, GB, VX) act as a solvent on most paints. This may cause peeling, dissolution, blistering, and discoloring at the leak area (U.S. Army, 1997).
Laboratory agent containers should be stored in a single containment system within an approved laboratory hood (SBCCOM, 1999). Storage of larger quantities should be in a double containment system (SBCCOM, 1999). Large quantities should be stored in one ton steel containers, or other approved containers (SBCCOM, 1999; (U.S. Army, 1997). "Ton containers of bulk agents will be stored in a horizontal position with the container oriented so that the valves are in vertical alignment"(U.S. Army, 1997). Glass is appropriate for Research, Development, Test, and Evaluation (RDTE) quantities (SBCCOM, 1999).
- ROOM/CABINET RECOMMENDATIONS
Tabun will decompose at 65 degrees C within 3 months and will completely decompose after 195 minutes at 150 degrees C (SBCCOM, 1999). Exits must be clearly marked to allow for rapid evacuation (SBCCOM, 1999). Chemical showers and eye wash stations must be provided (SBCCOM, 1999). "Structures used for the storage of agent-filled items will have floors and floor surfacing which can de decontaminated" (U.S. Army, 1997). "Sites should be selected that are not in proximity to surface water sources and which are not located over underground water sources that could become contaminated" (U.S. Army, 1997). "Construction materials such as wood or other porous materials that absorb agent are difficult to decontaminate and should not be used in the construction of buildings where agent is to be stored, handled, or processed" (U.S. Army, 1997). "Buildings and/or equipment will be arranged according to the sequence of operations. Such an arrangement will make it possible to keep handling of agents at a minimum and will minimize the necessity for transferring of agents through nonagent areas" (U.S. Army, 1997).
Tabun will react with water and steam to produce corrosive and toxic vapors (SBCCOM, 1999). Heat will cause tabun to decompose and form highly toxic fumes of phosphorus oxides, nitrogen oxides, and hydrogen cyanide (SBCCOM, 1999). Tabun is slightly corrosive to steel (RRIS , 2001).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- When responding to fires where chemical agents are stored, full firefighter protective clothing should be worn. Rescue/reconnaissance personnel should wear appropriate levels of protective clothing (SBCCOM, 1999).
- Laboratory operations require lab coats and gloves be worn. An approved respirator should be readily available. If handling contaminated animals, wear foot and head covers, and clean smocks (SBCCOM, 1999).
- "The use of personnel protective clothing and equipment (PCE) is the least desirable method of complying with airborne exposure limits. Efforts will be made to reduce dependence upon PCE in agent operating environments through the increased use of engineering and administrative controls such as ventilation, isolation, remote operations, remove monitoring, and elimination of a nonessential entries into agent areas" (U.S. Army, 1997).
- "Do not allow an individual to reenter the area to conduct the operation after the maximum wear time has been reached. However, the local medical authority may use discretion to vary the wear time" (U.S. Army, 1997).
- Real-time, low-level monitors with an alarm are required. If a monitor is not present, it should be assumed the atmosphere is Immediately Dangerous to Life and Health (SBCCOM, 1999).
- Editor's Note: Refer to the following document for information regarding the U.S. Department of Defense's Mission Oriented Protective Posture (MOPP) procedures and chemical protective equipment (CPE). Particular information is provided on the MOPP IV CPE ensemble.
US ARMY - PERSONNEL PROTECTIVE CLOTHING AND EQUIPMENT. This document is an assembly of sections containing information about Personal Protective Clothing and Equipment from U.S. Army publication "Toxic Chemical Agent Safety Standards"; Document Number: PAM 385-61. Unclassified. 31 March 1997. It is not, and should not be considered a complete copy of this publication.
EYE/FACE PROTECTION
- Chemical goggles are minimal protection and should be worn. If there is a potential situation for splash hazards, use goggles and a face shield (SBCCOM, 1999).
RESPIRATORY PROTECTION
- Respiratory protection is required (SBCCOM, 1999).
- When there is a potential danger of oxygen deficiency, and when directed by a chemical accident/incident operations officer or by a fire chief, a NIOSH- approved positive-pressure, full face piece self-contained breathing apparatus should be worn (SBCCOM, 1999).
- "The protective mask canister/filter will not be used for more than two hours when the mask has been worn in an area known to be above the AEL" (U.S. Army, 1997).
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 77-81-6.
ENGINEERING CONTROLS
- Local exhaust is mandatory. It must to filtered and scrubbed to limit excessive concentrations, and meet local, state and federal regulations (SBCCOM, 1999).
- Laboratory hoods need to have an average inward face velocity of 100 linear feet per minute plus or minus 20% with the velocity at any point not deviating from the average face velocity by more than 20% (SBCCOM, 1999).
- Existing laboratory hoods should have an inward face velocity of 150 linear feet per minute, plus or minus 20% (SBCCOM, 1999).
- Cross-drafts should not exceed 20% of the inward face velocity (SBCCOM, 1999).
- Laboratory operations should be performed at least 20 cm inside the hood face (SBCCOM, 1999).
- Visual smoke tests can be administered to evaluate the performance of the hood. Hood performance tests should be conducted semiannually, after any maintenance procedures, or after modifications have been installed (SBCCOM, 1999).
- Recirculation of exhaust air from chemical areas is prohibited. Connection between areas through the ventilation system is also prohibited (SBCCOM, 1999).
- Emergency back up power must be provided (SBCCOM, 1999).
-PHYSICAL HAZARDS
FIRE HAZARD
POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) Combustible material: may burn but does not ignite readily. When heated, vapors may form explosive mixtures with air: indoors, outdoors and sewers explosion hazards. Those substances designated with a "P" may polymerize explosively when heated or involved in a fire. Contact with metals may evolve flammable hydrogen gas. Containers may explode when heated. Runoff may pollute waterways. Substance may be transported in a molten form.
Evacuate all persons not involved in the fire-fighting efforts (SBBCOM, 1999). Contain warfare agent fires to prevent spreading to uncontrolled areas (SBCCOM, 1999). When responding to fires where chemical agents are stored, full firefighter protective clothing should be worn. Rescue/reconnaissance personnel should wear appropriate levels of protective clothing (SBCCOM, 1999).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS77-81-6 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Dry chemical, CO2, alcohol-resistant foam or water spray. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire.
- NFPA Extinguishing Methods for CAS77-81-6 (NFPA, 2002):
- Fog, foam, water mist, and CO2 are effective fire extinguishing agents. Do not use any fire-fighting methods that may cause the agent to splash or spread (SBCCOM, 1999).
- Fire may destroy most of the agent but measures must be taken to prevent the agent or contaminated liquids from entering the sewers and other areas (SBCCOM, 1999).
When tabun is heated to decomposition, it may emit oxides of nitrogen, oxides of phosphorus, carbon monoxide, and hydrogen cyanide (SBCCOM, 1999).
DUST/VAPOR HAZARD
- Tabun will react with water and steam to produce corrosive and toxic vapors (SBCCOM, 1999).
REACTIVITY HAZARD
- Heat will cause tabun to decompose and form highly toxic fumes of phosphorus oxides, nitrogen oxides, and hydrogen cyanide (SBCCOM, 1999).
- Tabun will react with water and steam to produce corrosive and toxic vapors (SBCCOM, 1999).
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. DOT ID No. 2810 - GA when used as a weapon SMALL SPILLS LARGE SPILLS
DOT ID No. 2810 - Tabun when used as a weapon SMALL SPILLS LARGE SPILLS
- SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
- PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate enclosed areas.
- Evacuate all persons not involved in the fire-fighting efforts (SBBCOM, 1999).
- AIHA ERPG Values for CAS77-81-6 (AIHA, 2006):
- DOE TEEL Values for CAS77-81-6 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Ethyl dimethylamidocyanophosphate (Tabun, GA) TEEL-0 (units = ppm): 0.000125 TEEL-1 (units = ppm): 0.00042 TEEL-2 (units = ppm): 0.0053 TEEL-3 (units = ppm): 0.039 Definitions: TEEL-0: The threshold concentration below which most people will experience no adverse health effects. TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure. TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape. TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.
- AEGL Values for CAS77-81-6 (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):
Listed as: Nerve agent GA Final Value: AEGL-1 10 min exposure: ppm: 0.001 ppm mg/m3: 0.0069 mg/m(3)
30 min exposure: ppm: 0.0006 ppm mg/m3: 0.004 mg/m(3)
1 hr exposure: ppm: 0.00042 ppm mg/m3: 0.0028 mg/m(3)
4 hr exposure: ppm: 0.00021 ppm mg/m3: 0.0014 mg/m(3)
8 hr exposure: ppm: 0.00015 ppm mg/m3: 0.001 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: Nerve agent GA Final Value: AEGL-2 10 min exposure: ppm: 0.013 ppm mg/m3: 0.087 mg/m(3)
30 min exposure: ppm: 0.0075 ppm mg/m3: 0.05 mg/m(3)
1 hr exposure: ppm: 0.0053 ppm mg/m3: 0.035 mg/m(3)
4 hr exposure: ppm: 0.0026 ppm mg/m3: 0.017 mg/m(3)
8 hr exposure: ppm: 0.002 ppm mg/m3: 0.013 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: Nerve agent GA Final Value: AEGL-3 10 min exposure: ppm: 0.11 ppm mg/m3: 0.76 mg/m(3)
30 min exposure: ppm: 0.057 ppm mg/m3: 0.38 mg/m(3)
1 hr exposure: ppm: 0.039 ppm mg/m3: 0.26 mg/m(3)
4 hr exposure: ppm: 0.021 ppm mg/m3: 0.14 mg/m(3)
8 hr exposure: ppm: 0.015 ppm mg/m3: 0.1 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 CAS77-81-6 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) ELIMINATE all ignition sources (no smoking, flares, sparks or flames in immediate area). Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 153 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection. fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
Laboratory Spill: A minimum of 56 grams of decontamination solution is needed for every gram of spilled tabun. The spilled agent is slowly added to the decontamination solution while it is agitated. Agitation must continue for at least one hour. Allow the solution to react for 24 hours. After the 24 hours, titrate the solution to a pH between 10 and 12. Add additional bleach to eliminate the alpha-Chloroacetophenone during the hydrolysis (SBCCOM, 1999). Laboratory Spill: "Areas where liquid agent has been spilled will be clearly identified and controlled to prevent inadvertent access by unauthorized personnel" (U.S. Army, 1997). Laboratory Spill: Only personnel in full protective clothing are allowed in areas where there has been a spill or release of chemical agents (SBCCOM, 1999). Laboratory Spill: "The material must be encapsulated so that the concentration of agent on the outside of the encapsulating material does not exceed the AEL" (U.S. Army, 1997). Laboratory Spill: Place the neutralized substance and contaminated clothing into a DOT- approved container, cover the material with the decontaminating solution, decontaminate the outside, and label the sealed container according to EPA and DOT regulations (SBCCOM, 1999). Laboratory Spill: Scoop the neutralized substance into a DOT-approved container, cover the material with the decontaminating solution, decontaminate the outside, and label the sealed container according to EPA and DOT regulations (SBCCOM, 1999). Laboratory Spill: Leaking containers should be placed in a double containment system with a sorbent material between the interior and exterior container (SBCCOM, 1999). Laboratory Spill: Dispose of the decontaminate according to local, state and Federal regulations (SBCCOM, 1999). Laboratory Spill: "The material must be encapsulated so that the concentration of agent on the outside of the encapsulating material does not exceed the AEL" (U.S. Army, 1997). Editor's Note: The decontamination solutions listed are not for dermal use.
Field Procedures: "Areas where liquid agent has been spilled will be clearly identified and controlled to prevent inadvertent access by unauthorized personnel" (U.S. Army, 1997). Field Procedures: Only personnel in full protective clothing are allowed in areas where there has been a spill or release of chemical agents (SBCCOM, 1999). Field Procedures: "Personnel who have been in areas of possible chemical agent exposure (normally, personnel downwind of an agent release or personnel who were in areas of known agent contamination) will remain at the installation for at least 30 minutes after leaving the area. They will then be observed for signs of agent exposure, and agent-related symptoms by the supervisor or his designated representative before departing the installation. If signs of possible exposure are noted the worker will be referred immediately to the medical family" (U.S. Army, 1997). Field Procedures: Cover spills with diatomaceous earth, vermiculite, clay, fine sand, sponges, cloth or paper towels (SBCCOM, 1999). Field Procedures: Use copious amounts of sodium hydroxide solution (a minimum 10 wt%) to decontaminate the area (SBCCOM, 1999). Field Procedures: If 10 wt% aqueous sodium hydroxide is not available, the following decontaminants may be substituted, and are listed in order of preference: Decontaminating Agent (DS2), Sodium Carbonate, and Supertropical Bleach Slurry (STB). DS2 is a combination of diethylenetriamine (70%), ethylene glycol monomethyl ether (28%), and sodium hydroxide (2%) (SBCCOM, 1999). Field Procedures: Treat the decontamination solution with excess bleach to destroy the hydrogen cyanide produced during hydrolysis (SBCCOM, 1999). Field Procedures: Scoop the neutralized substance into a DOT-approved container, cover the material with the decontaminating solution, decontaminate the outside, and label the sealed container according to EPA and DOT regulations (SBCCOM, 1999). Field Procedures: Leaking containers should be placed in a double containment system with a sorbent material between the interior and exterior container (SBCCOM, 1999). Field Procedures: Dispose of the decontaminate according to local, state and Federal regulations (SBCCOM, 1999). Field Procedures: "The material must be encapsulated so that the concentration of agent on the outside of the encapsulating material does not exceed the AEL" (U.S. Army, 1997). Editor's Note: The decontamination solutions listed are not for dermal use. Editor's Note: Do not mix DS2 and STB as a fire might result.
Some decontamination solutions are considered hazardous waste and must be disposed of according to RCRA and local health department regulations (SBCCOM, 1999). 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.
Open pit burning, or burying the chemical agent and items contaminated with the agent is strictly prohibited (U.S. Army, 1997). Detoxified chemical agents (using recommended army procedures) can be destroyed in an EPA approved incinerator according to provisions listed by the Federal, State, or local Resource Conservation and Recovery Act regulations (RCRA) (SBCCOM, 1999). Congress passed Pub. L. 99-145 (50 USC 1512) which mandates the destruction of sarin, VX, tabun, Lewisite, sulfur mustard, and (bis(2-chloroethylthioethyl)ether) by September 30, 1994 (CDC, 1988).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Chemical weapons, including tabun, have been dumped in oceans around the world. Portions of 2 barge loads of tabun were dumped at the "Baker" site off the coast of South Carolina in 1946 (Mitretek, 2000).
- Tabun was also dumped in the Baltic Sea, approximately 15 miles northeast of the Danish island of Bornholm (Mitretek, 2000).
- The stability of chemical agents is dependent on weather variables such as wind, temperature, temperature gradient, humidity, and precipitation. The magnitude of the effect of each variable depends upon the synoptic situation and is locally influenced by topography, vegetation, soil, and may also determine possible downwind hazards (U.S. Army, 1997).
ENVIRONMENTAL FATE AND KINETICS
No information on concentrations or atmospheric fate was available (Munro et al, 1999). Under average weather conditions, liquid tabun will persist for 1-2 days It evaporates about 20 times more slowly than water (Munro et al, 1999). "Weather (particularly temperature, temperature gradient, windspeed, and direction) directly influences the effectiveness and persistency of an agent" (U.S. Army, 1997). "The evaporation of liquid chemical agents increases as the temperature rises" (U.S. Army, 1997). "High winds increase the rate of evaporation of liquid chemical agents and dissipate chemical clouds more rapidly than low winds" (U.S. Army, 1997). "Wind controls the travel of chemical clouds" (U.S. Army, 1997).
SURFACE WATER At 20 degrees C, the half-life of tabun in freshwater is longer than in seawater (Munro et al, 1999). It is expected no volatilization will occur from water (Munro et al, 1999). Tabun was dispersed on the snow in Norway and persisted 2 weeks after the application, but was not detected 4 weeks later (Munro et al, 1999).
TERRESTRIAL Field studies have shown that 50% of tabun applied to soil will evaporate in 1.71 hours, and 90% will evaporate in 4.66 hours (HSDB , 2001). It is expected that hydrolysis is the dominant environmental degradation process in moist soils (HSDB , 2001). "Under stable conditions, chemical clouds tend to flow over rolling terrain around large hills and up and down valleys" (U.S. Army, 1997).
ABIOTIC DEGRADATION
- Tabun solutions of neutral pH hydrolyze more slowly than acidic and basic solutions (Munro et al, 1999).
- The rate of hydrolysis increases as the temperature increases (Munro et al, 1999).
- The half-life of tabun at 20 degrees C and pH 7.4 is estimated at 8 hours; at neutral pH at 25 degrees C persists in water for 14-28 hours (Munro et al, 1999).
- A half-life of 14 hours is reported at pH 3 and 2.5 hours at pH 5. No temperature was given (Munro et al, 1999).
- As tabun hydrolyzes and approaches a pH 4-5, acidic degradation products are formed (Munro et al, 1999).
- Tabun hydrolysis products and contaminants are (Munro et al, 1999):
O Ethyl-N,N-diemthylamidophosphonic acid Dimethylphosphoramidate Dimethylphosphoramidocyanidate Phosphrorcyanidate Phosphonic acid Ethyl phosphonic acid Dimethylamine Ethylphosphonyl cyanidate
BIODEGRADATION
- Tabun may be microbially degraded in soil via O-dealkylation and C-dealkylation. It is possible for nitrile hydrolysis and N-dealkylation to occur (Munro et al, 1999).
BIOACCUMULATION
ENVIRONMENTAL TOXICITY
- No terrestrial exotoxicity information is available (Munro et al, 1999).
- Tabun is highly toxic to aquatic organisms (Munro et al, 1999).
- AQUATIC TOXICITY (Munro et al, 1999):
LC50 - (WATER) GREEN SUNFISH (Lepomis cyanellus): 0.7 mg/L for 20 M LC50 - (WATER) FATHEAD MINNOWS (Pimephales promelas): 0.6 mg/L for 20M LC50 - (WATER) GOLDFISH (Carassius auratus): 1.3 mg/L for 20M
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Tabun is a clear, colorless to brown, liquid. It is tasteless and has a fruity odor (SBCCOM, 1999).
- It is chemically similar to organophosphate pesticides (USACHPPM , 2001).
VAPOR PRESSURE
- 0.057 mm Hg (at 25 degrees C) (SBCCOM, 1999)
- 0.037 mm Hg (at 20 degrees C) (Munro et al, 1999)
BOILING POINT
- 248 degrees C; 478 degrees F (at 760 mmHg) (SBCCOM, 1999)
FLASH POINT
- 78 degrees C (closed cup) (SBCCOM, 1999)
SOLUBILITY
Tabun is slightly soluble with water (SBCCOM, 1999). 9.8 (at 0 degrees C) (SBCCOM, 1999) 7.2 (at 20 degrees C) (SBCCOM, 1999)
HENRY'S CONSTANT
- 1.52 x 10(-7) atm-m(3)/mol (calculated) (Munro et al, 1999)
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