AMITROLE
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
AMEROL 3-AMINO-1H-1,2,4-TRIAZOLE 3-AMINO-S-TRIAZOLE AMINO TRIAZOLE 2-AMINOTRIAZOLE 3-AMINOTRIAZOLE 2-AMINO-1,3,4-TRIAZOLE 3-AMINO-1,2,4-TRIAZOLE AMINOTRIAZOLE AMINOTRIAZOLE (PLANT REGULATOR) AMINO TRIAZOLE WEEDKILLER AMINOTRIAZOL-SPRITZPULVER AMITOL AMITRIL AMITRIL TL AMITROL AMITROL 90 AMITROLE AMITROL-T AMIZINE AMIZOL AMIZOL D AMIZOL DP NAU AMIZOLE AMIZOL F AT AT LIQUID AT-90 3,A-T ATA AZAPLANT AZAPLANT KOMBI AZOLAN AZOLE CAMPAPRIM A 1544 CHEMPAR AMITROLE CYTROL CYTROL AMITROL-T CYTROLE DIUROL DIUROL 5030 DOMATOL DOMATOL 88 ELMASIL EMISOL EMISOL 50 EMISOL F FENAMINE FENAVAR HERBIDAL TOTAL HERBIZOLE 1H-1,2,4-TRIAZOL-3-AMINE 1H-1,2,4-TRIAZOLE-3-YLAMINE KLEER-LOT ORGA-414 RADOXONE TL RAMIZOL SIMAZOL SOLUTION CONCENTREE T271 S-TRIAZOLE, 3-AMINO- TRIAZOLAMINE TRIAZOLE(1,2,4), 3-AMINO-4H USTINEX VOROX VOROX AA VOROX AS WEEDAR ADS WEEDAR AT WEEDAZIN WEEDAZIN ARGINIT WEEDAZOL WEEDAZOLE WEEDAZOL GP2 WEEDAZOL SUPER WEEDAZOL T WEEDAZOL TL WEEDEX GRANULAT WEEDOCLOR X-ALL X-ALL LIQUID
IDENTIFIERS
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures.
SYNONYM REFERENCE
- (EPA, 1988)EXTOXNET, 1998;(HSDB , 1998; Lewis, 1993)LOLI, 1998;(NIOSH , 1998; RTECS , 1998)
USES/FORMS/SOURCES
Amitrole is used as: a non-selective post-emergence, translocated herbicide; plant growth regulator; and defoliant (for cotton). This compound's use on food crops is not permitted in the US (Ashford, 1994; Budavari, 1996; Grant, 1993; Lewis, 1993; Sittig, 1991). Amitrole is effective in eliminating woody plants, including coniferous and hardwood varieties. It is utilized as a contact spray for control of herbaceous perennials as well as most annual broadleaf grasses and weeds (Clayton & Clayton, 1994). Likely non-crop application scenarios include use for: drainage ditches, marshes, ornamentals, rights-of-way, and around agricultural, commercial, domestic, industrial, and recreational premises (EPA, 1988). Amitrole is applied as a foliar spray for broadcast, spot or directed treatments, and can be dispersed by aerial or ground equipment (EPA, 1988).
Amitrole is available as a wettable powder, soluble concentrate, and water dispersable granules (EXTOXNET, 1998). Commercially Available Formulations (EPA, 1988): Flowable Concentrate: 0.33 lb/gal, 0.44 lb/gal, 1% Pressurized Liquid: 0.36%, 1% Soluble Concentrate (Liquid): 0.3 lb/gal, 2 lb/gal Soluble Concentrate (Solid): 50%, 90% Technical: 90%, 95% Wettable Powder: 15%, 25%
SYNONYM EXPLANATION
- This compound is primarily know by the synonym "amino-triazole" in Great Britain, France, New Zealand, and the former U.S.S.R. (EXTOXNET, 1998).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Amitrole may be irritating to the eyes, skin, and mucous membranes. Signs and symptoms following exposure may include skin rash, anorexia, vomiting, diarrhea, muscle spasms, pulmonary edema, ataxia, lassitude, CNS depression, and suppression of thyroid function.
- In experimental animals, effects of overexposure have included extreme depression, difficulty breathing, clonic muscle spasms, coma, and death due to cardiac and circulatory failure. Thyroid and liver tumors have also been noted.
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Highly toxic, may be fatal if inhaled, swallowed or absorbed through skin. Avoid any skin contact. Effects of contact or inhalation may be delayed. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance;give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
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 water. If this chemical penetrates the clothing, immediately remove the clothing and wash the skin with water. If symptoms occur after washing, get medical attention immediately. 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, and thyroid [in animals: liver, thyroid and pituitary gland tumors] (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.
DERMAL EXPOSURE DECONTAMINATION: Remove contaminated clothing and jewelry and place them in plastic bags. Wash exposed areas with soap and water for 10 to 15 minutes with gentle sponging to avoid skin breakdown. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999). Treat dermal irritation or burns with standard topical therapy. Patients developing dermal hypersensitivity reactions may require treatment with systemic or topical corticosteroids or antihistamines.
EYE EXPOSURE DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility.
ORAL EXPOSURE Because of the potential for gastrointestinal tract irritation or CNS depression, do NOT induce emesis. Significant esophageal or gastrointestinal tract irritation or burns may occur following ingestion. The possible benefit of early removal of some ingested material by cautious gastric lavage must be weighed against potential complications of bleeding or perforation. 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. 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.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
- The minimum lethal human dose to this agent has not been delineated.
Amitrole is a confirmed animal carcinogen with experimental carcinogenic, tumorigenic, and neoplastigenic data. The International Agency for Research on Cancer (IARC) rates amitrole as Animal Sufficient Evidence and Human Inadequate Evidence. The National Toxicology Program anticipates this compound to be a carcinogen (NTP's 7th Annual Report on Carcinogens, 1992) (ACGIH, 1991; Budavari, 1996; Clayton & Clayton, 1993; Hathaway et al, 1996; Lewis, 1996). In one small cohort study of Swedish railroad workers, a statistically significant excess of all cancers was noted when workers were exposed to amitrole and chlorophenoxy herbicides (eg, 2,4-D, 2,4,5-T, diuron, monuron). This excess was not seen among those exposed primarily to amitrole (ACGIH, 1991; Hathaway et al, 1996).
MAXIMUM TOLERATED EXPOSURE
- The maximum tolerated human exposure to this agent has not been delineated.
- In healthy persons as well as those with hyperthyroidism, a single dose of 100 mg amitrole inhibited the uptake of iodine-131 by the thyroid for 24 hours. A dose of 10 mg amitrole had only slight effect and can be seen as a threshold dose (ACGIH, 1991; Clayton & Clayton, 1994).
- A 39-year-old woman attempted suicide by ingesting a mixture which included amitrole. The amount of amitrole ingested was 20 mg/kg. The woman did not become ill. Unchanged amitrole at a concentration of 1000 ppm was found in the urine (Clayton & Clayton, 1994; EXTOXNET, 1998).
- Carcinogenicity Ratings for CAS61-82-5 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A3 ; Listed as: Amitrole A3 :Confirmed Animal Carcinogen with Unknown Relevance to Humans: The agent is carcinogenic in experimental animals at a relatively high dose, by route(s) of administration, at site(s), of histologic type(s), or by mechanism(s) that may not be relevant to worker exposure. Available epidemiologic studies do not confirm an increased risk of cancer in exposed humans. Available evidence does not suggest that the agent is likely to cause cancer in humans except under uncommon or unlikely routes or levels of exposure.
EPA (U.S. Environmental Protection Agency, 2011): Not 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): 3 ; Listed as: Amitrole 3 : The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.
NIOSH (National Institute for Occupational Safety and Health, 2007): Ca ; Listed as: Amitrole MAK (DFG, 2002): Category 3B ; Listed as: Amitrole Category 3B : Substances for which in vitro or animal studies have yielded evidence of carcinogenic effects that is not sufficient for classification of the substance in one of the other categories. Further studies are required before a final decision can be made. A MAK value can be established provided no genotoxic effects have been detected. (Footnote: In the past, when a substance was classified as Category 3 it was given a MAK value provided that it had no detectable genotoxic effects. When all such substances have been examined for whether or not they may be classified in Category 4, this sentence may be omitted.)
NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS61-82-5 (U.S. Environmental Protection Agency, 2011):
References: ACGIH, 1991 Budavari, 1996 Clayton & Clayton, 1994 EXTOXNET, 1998 Hathaway et al, 1996 Lewis, 1996 RTECS, 1998 Note: Specific references are included below when significantly differing values are reported for the same animal and route. LD- (ORAL)SHEEP: LD50- (ORAL)LABORATORY_QUAIL: LD50- (INTRAPERITONEAL)MOUSE: LD50- (INTRAVENOUS)MOUSE: LD50- (ORAL)MOUSE: 15,000 mg/kg (Clayton & Clayton, 1994; EXTOXNET, 1998) 14,700 mg/kg (ACGIH, 1991; RTECS, 1998; Lewis, 1996) 11,000 mg/kg (ACGIH, 1991; Clayton & Clayton, 1994; Hathaway et al, 1998)
LD50- (SKIN)RABBIT: LD50- (ORAL)RAT: 1100 mg/kg (RTECS, 1998) 25.0 g/kg (ACGIH, 1991; Budavari, 1996) 24,600 mg/kg (Clayton & Clayton, 1994; EXTOXNET, 1998)
LD50- (SKIN)RAT: TD- (ORAL)MOUSE: TD- (ORAL)RAT: TDLo- (ORAL)MOUSE: TDLo- (SUBCUTANEOUS)MOUSE: TDLo- (ORAL)RAT:
CALCULATIONS
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS61-82-5 (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 CAS61-82-5 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS61-82-5 (National Institute for Occupational Safety and Health, 2007):
Listed as: Amitrole REL: IDLH: Not Listed
- OSHA PEL Values for CAS61-82-5 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS61-82-5 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS61-82-5 (U.S. Environmental Protection Agency, 2010):
Listed as: 1H-1,2,4-Triazol-3-amine Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Amitrole Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS61-82-5 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS61-82-5 (U.S. Environmental Protection Agency, 2010b):
Listed as: Amitrole P or U series number: U011 Footnote: Listed as: 1H-1,2,4-Triazol-3-amine P or U series number: U011 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 CAS61-82-5 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS61-82-5 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS61-82-5 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS61-82-5 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions (49 CFR 172.101, 2005):
- ICAO International Shipping Name (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS61-82-5 (NFPA, 2002):
-HANDLING AND STORAGE
HANDLING
- All precautions for handling carcinogens should be observed when dealing with amitrole (HSDB , 1998).
- This compound is stable at temperatures of up to 100 degrees C (EPA, 1988).
STORAGE
- ROOM/CABINET RECOMMENDATIONS
This compound needs to be stored in a cool, dry, place or a refrigerator (Sittig, 1991). Store amitrole at room temperature (HSDB , 1998).
Protect amitrole from air and light (will cause degradation) as well as strong oxidizers (incompatible) (Clayton & Clayton, 1994; NIOSH , 1998; Sittig, 1991).
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
- Appropriate personal protective clothing should be worn to prevent contact with amitrole. Contaminated or wet clothing should be removed and replaced. Workers should wash at the end of each work shift. Persons whose clothing may have been contaminated should change into uncontaminated clothing before leaving the job site (NIOSH , 1998).
EYE/FACE PROTECTION
- Appropriate eye protection should be worn to prevent contact with this compound. In areas where there is any possibility that persons may be exposed to this compound, eyewash fountains should be provided (NIOSH , 1998).
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
- "At any exposure level, use an MSHA/NIOSH approved supplied-air respirator with a full facepiece operated in the positive pressure mode or with a full facepiece, hood, or helmet in the continuous flow mode, or use a MSHA/NIOSH approved self-contained breathing apparatus with a full facepiece operated in pressure-demand or other positive pressure mode." (Sittig, 1991)
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 61-82-5.
ENGINEERING CONTROLS
- A facility for quickly drenching the body, or body parts, with water needs to be provided within the immediate work area. This is intended to quickly remove amitrole from any body areas likely to be exposed. In some instances a hose connected to a sink may be permissible, in others a full deluge shower may be required (NIOSH , 1998).
-PHYSICAL HAZARDS
FIRE HAZARD
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures. POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Non-combustible, substance itself does not burn but may decompose upon heating to produce corrosive and/or toxic fumes. Containers may explode when heated. Runoff may pollute waterways.
Amitrole is a noncombustible solid (NIOSH , 1998). This compound may be dissolved in flammable liquids (NIOSH , 1998).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS61-82-5 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material. Use water spray or fog; do not use straight streams.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS61-82-5 (NFPA, 2002):
- As this compound is noncombustible, choose a fire extinguishing agent suitable for the type of surrounding fire (Sittig, 1991).
DUST/VAPOR HAZARD
- Toxic fumes of nitrogen oxides are released when this compound is heated to decomposition (Lewis, 1996).
REACTIVITY HAZARD
- Amitrole is decomposed by light and is incompatible with strong oxidizers (Clayton & Clayton, 1994; NIOSH , 1998).
- This compound reacts with most acids and bases to form salts, reacts with aldehydes and ketones to form derivatives with possible biologic activity, and is oxidized to azotriazole(Clayton & Clayton, 1994).
- It sublimes under reduced pressure (EPA, 1988).
- This compound is mildly corrosive to aluminum, copper (as well as copper alloys), and iron (HSDB , 1998).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 25 to 50 meters (80 to 160 feet) in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
- PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas.
- AIHA ERPG Values for CAS61-82-5 (AIHA, 2006):
- DOE TEEL Values for CAS61-82-5 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Amitrole TEEL-0 (units = mg/m3): 0.2 TEEL-1 (units = mg/m3): 0.6 TEEL-2 (units = mg/m3): 75 TEEL-3 (units = mg/m3): 500 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 CAS61-82-5 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS61-82-5 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Cover with plastic sheet to prevent spreading. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
Isolate and contain spills involving amitrole. Spilled material and sorbent media may be packaged in epoxy-lined drums (Sittig, 1991).
Destruction may be accomplished by incineration or microwave plasmic treatment. Permanganate oxidation is also a possibility, but amitrole is resistant to the action of oxidizing agents. Burning amitrole with polyethylene is reported to result in >99% decomposition (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
- As an agricultural chemical, amitrole is most likely to enter the environment by way of its production, formulation, and application. This compound does not naturally occur in the environment (ACGIH, 1991; Howard, 1991; Sittig, 1991).
ENVIRONMENTAL FATE AND KINETICS
In the atmosphere, vapor-phase amitrole will rapidly react with photochemically produced hydroxyl radicals; estimated half-life of 3.8 days at 25 degrees C. This compound will not directly photolyze nor react with ozone (Howard, 1991). Atmospheric Half-Life (Scientific judgement based upon estimated rate constant for vapor phase reaction with hydroxyl radicals in air) (Howard et al, 1991):
SURFACE WATER In natural waters, degradation of amitrole may be possible by oxidation with photochemically produced peroxy radicals or by photosensitized photolysis. It is persistent in hydrosoil and pond water. Adsorption to hydrosoil may be a significant transport mechanism; an initial maximum half-life of 68 days was noted when amitrole was applied to an outdoor pond with persistence exceeding 200 days. Direct photolysis, hydrolysis, and volatilization are not expected to be important processes (EPA, 1988; Howard, 1991; Sittig, 1991). Surface Water Half-Life (Scientific judgement based upon estimated aqueous aerobic biodegradation half-life.) (Howard et al, 1991): Ground Water Half-Life (Scientific judgement based upon estimated aqueous aerobic biodegradation half-life) (Howard et al, 1991):
TERRESTRIAL At the recommended herbicidal application level, amitrole is reported to have a resultant average persistence of approximately 2-4 weeks. The half-life in loam soil has been measured to be 1 month at 15 degrees C (under laboratory conditions). In warm, moist soil, microbial breakdown takes 2-3 weeks. Chemical degradation by reaction with metals or free radicals may be an important route. Amitrole possesses moderate potential for leaching into groundwater, as it is readily soluble in water and does not strongly adsorb to soil particulates. It is persistent in hydrosoil. Factors which affect the half-life as well as leaching are: temperature, moisture, clay content, and cation exchange capacity (unaffected by pH). Photodegradation and volatilization are not expected to be significant routes (EPA, 1988; EXTOXNET, 1998; Howard, 1991). Soil Half-Life (Scientific judgement based upon estimated aqueous aerobic biodegradation half-life.) (Howard et al, 1991):
BIODEGRADATION
- Microbial biodegradation is expected to be a significant route, although, it has not been demonstrated to be a rapid removal process in water (estimated half-life of approximately 40 days) (EPA, 1988; Howard, 1991).
- Aerobic Half-Life (Scientific judgement based upon reported soil and water half-lives.) (Howard et al, 1991):
- Anaerobic Half-Life (Scientific judgement based upon estimated aqueous aerobic biodegradation half-life.) (Howard et al, 1991):
BIOACCUMULATION
AQUATIC Amitrole is easily absorbed and quickly translocated to the leaves and roots of higher plants. Generally, plants are able to metabolize this compound in 1-4 weeks. Residues were not detected in crops planted in soil 1-50 days post application (EXTOXNET, 1998).
ENVIRONMENTAL TOXICITY
- Avian Toxicity (EPA, 1988; EXTOXNET, 1998; HSDB , 1998)
LD50 - (ORAL) MALLARD DUCK: 2000 mg/kg LC50 - (ORAL) MALLARD DUCK: >5000 ppm LD50 - (ORAL) JAPANESE QUAIL: >5000 ppm -- age 12D LC50 - (ORAL) RING-NECK PHEASANT: >5000 ppm -- age 10D
- Freshwater Fish Toxicity (EPA, 1988; HSDB , 1998)
LC50 - RAINBOW TROUT: >180 mg/L LC50 - BLUEGILL SUNFISH: >180 mg/L LC50 - BLUEGILL SUNFISH: 100 ppm for 48H -- conditions of bioassay not specified LC50 - GAMMARUS FASCIATUS/SCUD: >10 mg/L for 96H -- at 18 degrees C, static conditions without aeration LC50 - FATHEAD MINNOW: >100 mg/L for 96H -- weight 1.2 g, at 18 degrees C, static conditions without aeration LC50 - CHANNEL CATFISH: >160 mg/L for 96H -- weight 1.8 g, at 18 degrees C, static conditions without aeration
- Aquatic Organism Toxicity (HSDB , 1998)
LC50 - COTURNIX: >5000 ppm -- age 12D LC50 - CYRIDOPSIS VIDUA: 32,000 mcg/L for 48H -- conditions of bioassay not specified LC50 - DAPHNIA MAGNA: 30,000 mcg/L for 48H -- conditions of bioasssay not specified LC50 - ONCORHYNCUS KISUTCH: 325,000 mcg/L for 48H -- conditions of bioassay not specified
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Amitrole exists as an odorless, colorless to white, crystalline powder with a bitter taste (Ashford, 1994; Clayton & Clayton, 1994; EXTOXNET, 1998; Lewis, 1993; NIOSH , 1998).
- crystals from absolute ethanol, ethyl acetate, or water (Budavari, 1996; Lewis, 1996)
- hydrochloride form: crystals from alcohol (Budavari, 1996)
PH
- Aqueous solutions of amitrole are neutral (Budavari, 1996; EPA, 1988).
- Amitrole forms neutral aqueous solutions, but acts as a weak base with Kb of 1x10(-10) (HSDB , 1998).
VAPOR PRESSURE
- <0.000008 mmHg (NIOSH , 1998)
- 0.055 mmHg (at 20 degrees C) (Clayton & Clayton, 1994)
- <7.5x10(-6) mmHg (at 20 degrees C) (Howard, 1991; HSDB , 1998)
- <1 mPa (at 20 degrees C) (EXTOXNET, 1998)
SPECIFIC GRAVITY
- TEMPERATURE AND/OR PRESSURE NOT LISTED
SOLID: 1.14 (NIOSH , 1998) SOLID: 1.138 (Clayton & Clayton, 1994)
FREEZING/MELTING POINT
156-159 degrees C (Lewis, 1993) 157-159 degrees C (Ashford, 1994; Clayton & Clayton, 1994; Howard, 1991) 159 degrees C (Budavari, 1996; EPA, 1988; Lewis, 1996) 153-159 degrees C (ACGIH, 1991) 158-159 degrees C (Sittig, 1991) 157 degrees C (EXTOXNET, 1998) hydrochloride: 153 degrees C (Budavari, 1996)
BOILING POINT
FLASH POINT
- Not Applicable (NIOSH , 1998)
EXPLOSIVE LIMITS
SOLUBILITY
soluble (Ashford, 1994; Budavari, 1996; Lewis, 1993) 280,000 mg/L (Howard, 1991) 280,000 mg/L (at 23 degrees C) (EXTOXNET, 1998) 28 g/100 g water (at 25 degrees C) (EPA, 1988; HSDB , 1998) 28% (at 77 degrees F) (NIOSH , 1998)
soluble in acetone, chloroform, ethanol, methanol, nonpolar solvents, and some polar solvents (Ashford, 1994; Budavari, 1996; EPA, 1988; EXTOXNET, 1998; Lewis, 1993) sparingly soluble in ethyl acetate (Budavari, 1996) slightly soluble in acetonitrile and methylene chloride (HSDB , 1998) insoluble in acetone, benzene, carbon tetrachloride, diesel oil, ether, kerosene, and most hydrocarbons (ACGIH, 1991; Budavari, 1996; Clayton & Clayton, 1994; HSDB , 1998)
OCTANOL/WATER PARTITION COEFFICIENT
- Log Kow = -0.15 (Howard, 1991)
- Log Kow = -0.65 (calculated) (HSDB , 1998)
HENRY'S CONSTANT
- <3.0x10(-12) atm-m(3)/mol (estimated) (Howard, 1991)
SPECTRAL CONSTANTS
21258 (Sadtler Research Laboratories IR Grating Collection) (HSDB , 1998) Sadtler Reference Number: 8667 (IR, Prism) (HSDB , 1998)
OTHER/PHYSICAL
- NUCLEAR MAGNETIC RESONANCE
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