2,4,5-T
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
2,4,5-T ACETIC ACID, (2,4,5-TRICHLOROPHENOXY)- ACIDE 2,4,5-TRICHLORO PHENOXYACETIQUE (FRENCH) ACIDO (2,4,5-TRICLORO-FENOSSI)-ACETICO (ITALIAN) AMINE 2,4,5-T for RICE BCF-BUSHKILLER BRUSH-OFF 445 LOW VOLATILE BRUSH KILLER BRUSH RHAP BRUSHTOX DACAMINE DEBROUSSAILLANT CONCENTRE DEBROUSSAILLANT SUPER CONCENTRE DECAMINE 4T DED-WEED BRUSH KILLER DED-WEED LV-6 BRUSH KIL and T-5 BRUSH KIL DINOXOL ENVERT-T ESTERCIDE T-2 and T-245 ESTERON ESTERON 245 ESTERON 245 BE ESTERON BRUSH KILLER ESTERONE 245 FARMCO FENCE RIDER FENCE RIDER FORRON FORST U 46 FORTEX FRUITONE A INVERTON 245 KWAS 2,4,5-TROJCHLOROFENOKSYOCTOWY (POLISH) LINE RIDER PHORTOX REDDON REDDOX SPONTOX SUPER D WEEDONE TIPPON TORMONA TRANSAMINE TRIBUTON (2,4,5-TRICHLOOR-FENOXY)-AZIJNZUUR (DUTCH) TRICHLOROPHENOXYACETIC ACID 2,4,5-TRICHLOROPHENOXYACETIC ACID (2,4,5-TRICHLOROPHENOXY)ACETIC ACID (2,4,5-TRICHLOR-PHENOXY)-ESSIGSAEURE (GERMAN) TRINOXOL TRIOXON TRIOXONE U 46 VEON VEON 245 VERTON 2T VISKO RHAP LOW VOLATILE ESTER WEEDAR WEEDONE WEEDONE 2,4,5-T 2,4,5 TRICHLOROPHENOXY ACETIC ACID ESTER OR SALT
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
- (Budavari, 1989; RTECS , 1992)
USES/FORMS/SOURCES
It is used as a plant hormone, herbicide and defoliant (Sax & Lewis, 1987; HSDB , 1992). Use in the US has been restricted by the US Environmental Protection Agency (Sax & Lewis, 1987; HSDB , 1992). In March, 1985 the US Environmental Protection Agency terminated all registrations for the use of this herbicide on rice fields, orchards, sugarcane, rangeland and other non-crop sites. This follows the 1970 action of the Department of Agriculture halting the use of the pesticide on all food crops except rice (Budavari, 1989).
2,4,5-T is an odorless, colorless to tan, non-combustible, crystalline solid (ACGIH, 1986; Budavari, 1989). Commercial products are usually in the form of amines or esters, often in mixture with 2,4-D (Budavari, 1989).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- 2,4,5-T is a poison by ingestion and moderately toxic by other unspecified routes. It is readily absorbed by inhalation and ingestion routes, and absorbed slowly by skin contact. It is an experimental neoplastigen, tumorigen and teratogen. It may be a human and experimental carcinogen. 2,4,5-T causes reproductive effects. Mutagenic data exists.
- 2,4,5-T is a highly toxic chlorinated phenoxy acid herbicide which is rapidly excreted after ingestion. However, another source states that 2,4,5-T is of low-order acute toxicity.
- Chronic exposure is not necessarily more hazardous than acute exposure for laboratory animals.
- Signs of intoxication by 2,4,5-T include weakness, lethargy, anorexia, diarrhea, ventricular fibrillation and/or cardiac arrest and death.
- Most if not all occupational illness associated with 2,4,5-T has been found to be the result of product contamination with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)--for example, chloracne. TCDD is extremely toxic to animals, and exposure has also been associated with liver function impairment, peripheral neuropathy, personality changes, porphyria cutanea, hypertrichosis, and hyperpigmentation. The role of dioxin contaminants must always be considered in the discussion of 2,4,5-T toxicology.
- Chloracne from chlorodioxin contamination of 2,4,5-T has occurred in manufacturing plant workers but not in handlers of the commercially packaged herbicides.
- "Agent Orange", a half-and-half mixture of 2,4-D and 2,4,5-T, has been alleged to have caused cancer, birth defects and many other disease conditions. The contaminant of 2,4,5-T, known as 2,3,7,8-tetrachlorodioxin (TCDD) has been the putative cause of chronic adverse effects of Agent Orange. Although TCDD is, indeed, extremely toxic, the causal relationship between the chlorophenoxy herbicides and various chronic disease conditions in man remains unproven and controversial.
- Allegations of teratogenic and carcinogenic effects of 2,4,5-T and dioxins in man have not been confirmed.
Animal studies do not support the notion that 2,4,5-T itself is carcinogenic. Studies on cancer have found increased risks of 5.3, 6.8 and 3.96 for soft-tissue sarcoma, 7.7 and 6 for stomach cancer, 2.05 for lung cancer, 4.8 for lymphoma, 2.3 for all cancers combined, and 5.2 for liver cancer after exposure to 2,4,5-T or dioxin contaminants.
- In common with many other chemicals, 2,4,5-T and the contaminating dioxins (but apparently not 2,4-D), are teratogenic in laboratory animal species.
The teratogenicity of 2,4,5-T is due in part to 2,3,7,8-TCDD, which is present as a contaminant.
- The following information is for CHLOROPHENOXY COMPOUNDS in general:
- Limited data are available on exact toxic doses. These compounds appear to be moderately toxic to liver and kidneys, and sometimes to the central nervous system, skeletal muscle, and myocardium. Serious acute human poisonings have followed ingestions of multi-gram doses.
- 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.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
In rats fed diets containing 2000 ppm of 2,4,5-T (less than 0.05 TCDD), the minimal cumulative fatal dose was approximately 900 mg/kg (Proctor et al, 1988).
MAXIMUM TOLERATED EXPOSURE
Eleven men in two separate experiments experienced no clinical effects after ingestion of 5 mg/kg of 2,4,5-T. Most of the men reported a metallic taste lasting 1 to 2 hours after ingestion (Proctor et al, 1988). A study of 204 workers exposed from 1 month to 20 years to 2,4,5-T and its contaminants (concentrations unspecified) showed no evidence of increased risk for cardiovascular disease, hepatic disease, renal damage, central or peripheral nervous system effects, reproductive problems, or birth defects. Clinical evidence of chloracne persisted in 55.7%, and an association between exposure and history of upper gastrointestinal tract ulcer was found (Proctor et al, 1988).
- Carcinogenicity Ratings for CAS93-76-5 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: 2,4,5-T EPA (U.S. Environmental Protection Agency, 2011): Not Assessed under the IRIS program. ; Listed as: 2,4,5-Trichlorophenoxyacetic acid (2,4,5-T) IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: 2,4,5-T 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 CAS93-76-5 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 1x10(-2) mg/kg-day
Inhalation: Drinking Water:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS93-76-5 (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 CAS93-76-5 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS93-76-5 (National Institute for Occupational Safety and Health, 2007):
Listed as: 2,4,5-T REL: IDLH: IDLH: 250 mg/m3 Note(s): Not Listed
- OSHA PEL Values for CAS93-76-5 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
Listed as: 2,4,5-T (2,4,5-trichlorophenoxyacetic acid) Table Z-1 for 2,4,5-T (2,4,5-trichlorophenoxyacetic acid): 8-hour TWA: ppm: mg/m3: 10 Ceiling Value: Skin Designation: No Notation(s): Not Listed
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS93-76-5 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS93-76-5 (U.S. Environmental Protection Agency, 2010):
Listed as: 2,4,5-T Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: 2,4,5-T acid Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Acetic acid, (2,4,5-trichlorophenoxy)- Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS93-76-5 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS93-76-5 (U.S. Environmental Protection Agency, 2010b):
Listed as: Acetic acid, (2,4,5-trichlorophenoxy)- P or U series number: See F027 Footnote: Listed as: 2,4,5-T P or U series number: See F027 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 CAS93-76-5 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS93-76-5 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS93-76-5 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS93-76-5 (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 CAS93-76-5 (NFPA, 2002):
-HANDLING AND STORAGE
SUMMARY
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Keep in well-ventilated area (OHM/TADS , 1992). Do not store in freezing temperatures (HSDB , 1992).
Temperatures above 158 degrees C may cause sealed metal containers to burst (HSDB , 1992). Do not store near other agrochemicals or seeds (HSDB , 1992).
-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.
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 93-76-5.
-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.
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS93-76-5 (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 CAS93-76-5 (NFPA, 2002):
When heated to decomposition, 2,4,5-T emits toxic fumes of chlorides; in addition, toxic gases and vapors such as phosgene and hydrogen chloride may be formed during combustion (HSDB , 1992; Sax & Lewis, 1989).
DUST/VAPOR HAZARD
- When heated to decomposition, 2,4,5-T emits toxic fumes of chlorides; in addition, toxic gases and vapors such as phosgene and hydrogen chloride may be formed during combustion (HSDB , 1992; Sax & Lewis, 1989).
REACTIVITY HAZARD
- When heated to decomposition, 2,4,5-T emits toxic fumes of chlorides; in addition, toxic gases and vapors such as phosgene and hydrogen chloride may be formed during combustion (HSDB , 1992; Sax & Lewis, 1989).
- Tetrachlorodibenzo-p-dioxin may be formed during the burning of vegetation treated with 2,4,5-T (HSDB , 1992).
- 2,4,5-T is non-corrosive, but some oil-based formulations may be deleterious to painted surfaces (HSDB , 1992).
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 CAS93-76-5 (AIHA, 2006):
- DOE TEEL Values for CAS93-76-5 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Trichlorophenoxyacetic acid, 2,4,5- (2,4,5-T) TEEL-0 (units = mg/m3): 10 TEEL-1 (units = mg/m3): 10 TEEL-2 (units = mg/m3): 10 TEEL-3 (units = mg/m3): 250 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 CAS93-76-5 (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; 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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; 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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 CAS93-76-5 (National Institute for Occupational Safety and Health, 2007):
IDLH: 250 mg/m3 Note(s): Not Listed
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.
At the time of this review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices (HSDB , 1992). ENVIRONMENTAL CONSIDERATIONS - LAND SPILL (AAR, 1987) Dig a pit, pond, lagoon, or holding area to contain liquid or solid material. Cover solids with a plastic sheet to prevent dissolving in rain or fire fighting water.
ENVIRONMENTAL CONSIDERATIONS - WATER SPILL (AAR, 1987) Remove trapped material with suction hoses. If dissolved in region of 10 ppm or greater concentration, apply activated carbon at ten times the spilled amount. Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates.
2,4,5-T is a potential candidate for rotary kiln incineration, fluidized bed incineration, and liquid injection incineration (HSDB , 1992). Several metabolites in the metabolic pathway of 2,4,5-T have been shown to be either mutagenic or genotoxic. The bacteria strain Pseudomonas cepacia (AC1100) is reported to grow on 2,4,5-T as the sole carbon and energy source. An experiment was conducted to determine if these toxic by products are formed in toxic concentrations during biodegradation of 2,4,5-T. As the reaction proceeds the genotoxicity decreases and no mutagenic response was observed (George et al, 1992).
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Release of 2,4,5-T to the environment occurred during its past use as an herbicide and it can form in the environment as a hydrolysis product of its herbicide esters. Other sources of release may include losses during formulation, packaging, or disposal of 2,4,5-T, its esters and the acaracide, tetradifon. Since 2,4,5-T has a pKa of 2.88, it will be found in the dissociated form in all environmental media (HSDB , 1992).
- 2,4,5-T, 2,4-D, dichlorophenol, and 2,4,5-trichlorophenol all showed similar adsorption and desorption diffusion coefficients for volcanic soil, as measured by Fruenlich type isotherms (Susarla et al, 1993).
ENVIRONMENTAL FATE AND KINETICS
If released to the atmosphere, 2,4,5-T may exist in vapor form as fine droplets and adsorbed on air-borne particulates as a result of vapor phase adsorption, or as a result of wind erosion of treated soils. 2,4,5-T has the potential to undergo (a) direct photolysis due to ultraviolet absorption at greater than 290 nm, (b) reaction with photochemically generated hydroxyl radicals (estimated vapor phase half-life = 1.12 days), or (c) physical removal by settling or washing out in rainfall (HSDB , 1992). PHOTODECOMPOSITION: A laboratory study was conducted to determine the effect of hydrogen peroxide and iron ions on the decomposition of 2,4-D and 2,4,5-T. The process resulted in 40 to 70 percent conversion to carbon dioxide and quantitative dechlorination. The reaction was irradiated with visible light from a small UV component. The photo-assisted conversion to CO2 proceeded to completion in less than 2 hours, with hydrogen peroxide to herbicide molar ratios as low as 5 (Pignatello, 1992).
SURFACE WATER Since 2,4,5-T has a pKa of 2.88 at 25 degrees C, it will be dissociated in water. If released to water, photochemical decomposition and biodegradation of 2,4,5-T should be the dominant removal mechanisms. 2,4,5-Trichlorophenol is the primary degradation product of 2,4,5-T in water (HSDB , 1992). Data regarding the biodegradation of 2,4,5-T in soil suggest that biodegradation may contribute significantly to the degradation of 2,4,5-T in aquatic systems. The aquatic near surface half-life for direct photolysis has been calculated to be 15 days during summer at a latitude of 40 degrees. Humic substances can photosensitize 2,4,5-T and humic-induced photoreactions may dominate photodegradation processes when humic substance concentrations exceed 15 mg of organic carbon per liter. 2,4,5-T may also be degraded by photocatalytic processes involving iron species and peroxides (HSDB , 1992). The primary products of 2,4,5-T photodegradation are 2,4,5-trichlorophenol and 2-hydroxy-4,5-dichlorophenoxyacetic acid. Adsorption of 2,4,5-T to humic acids in suspended solids and sediments may be significant. Oxidation, chemical hydrolysis, volatilization, and bioaccumulation should not be significant (HSDB , 1992).
TERRESTRIAL If released to soil, 2,4,5-T is likely to biodegrade and its mobility is expected to vary from highly mobile in sandy soil and moderately mobile in clay and silt loams to slightly mobile in muck (due to adsorption to humic acids and other organic matter). Removal by biodegradation apparently limits the extent of leaching, however, and groundwater contamination is likely only by rapid flow through large channels and deep soil cracks (HSDB , 1992). 2,4,5-Trichlorophenol and 2,4,5-trichloroanisole are the primary degradation products of 2,4,5-T in soil. The anisole is apparently formed by microbial methylation of the phenol (HSDB , 1992). Chemical hydrolysis in moist soils should not be significant. The persistence of 2,4,5-T in soil is reported to vary from 14 to 300 days depending upon climatic conditions and population of soil microorganisms, but usually does not exceed one full growing season regardless of the application rate (HSDB , 1992). Degradation under anaerobic conditions is much slower than under aerobic conditions, thus 2,4,5-T persists longer in flooded soils (half-life of less than or equal to 48 weeks) than in field-moist soils (HSDB , 1992).
BIODEGRADATION
- The bacterium Phanerochaete chrysosporium was used to mineralize separate and mixed solutions of 2,4-D and 2,4,5-T. Eighty-two percent of the herbicides was biodegraded in high nitrogen and malt extract media. The mixtures degraded at a faster rate than the individual materials (Yadav & Reddy, 1993).
- Is bound to organic matter; 90% is gone within 6 months, 99% over 1 year after microbial destruction (Smith & Oehme, 1991).
- Is adsorbed to bottom sediments and destroyed by microbes (Wagner, 1983).
ENVIRONMENTAL TOXICITY
- Ecotoxicity Values (HSDB , 1992):
LC50 Salmo gairdneri (rainbow trout), 350 mg/L/96 hours, conditions of bioassay not given LC50 Lepomis macrochirus (bluegill), 0.50 mg/L/48 hours, conditions of bioassay not specified LC50 Lebistes reticulatus (guppy), 8 mg/L/48 hours, conditions of bioassay not specified LC50 Salmo gairdneri (rainbow trout), 1.3 mg/L/48 hours, conditions of bioassay not specified LC50 Salmo gairdneri (rainbow trout), 0.98 mg/L/96 hours in river water, renewal bioassay LC50 Morone saxatilis (striped bass), 14.6 mg/L/96 hours, static bioassay LC50 Banded killifish, 17.4 mg/L/96 hours, static bioassay LC50 Lepomis gibbosus (pumpkinseed), 20.0 mg/L/96 hours, static bioassay LC50 Morone americana (white perch), 16.4 mg/L/96 hours, static bioassay LC50 Anguilla rostrata (American eel), 43.7 mg/L/96 hours, static bioassay LC50 Cyprinus carpio (carp), 41.1 mg/L/96 hours, static bioassay LC50 Lebistes reticulatus (guppy), 28.1 mg/L/96 hours, static bioassay LD50 Anas platyrhynchos (mallard), male, oral, greater than 2000 mg/kg, age 3 months, sample purity: assumed to be technical grade LD50 Phasianus colchicus (pheasant), male, oral, 500 to 1000 mg/kg, age 3 months, sample purity: assumed to be technical grade No toxic effect was observed in Penaeus aztecus (brown shrimp) exposed to 1000 mcg/L/48 hours of technical grade No effect on survival was observed in Fundulus similis (longnose killifish) exposed to 50,000 mcg/L/48 hours of technical grade No effect was observed in Mugil cephalus (striped mullet) exposed to 50,000 mcg/L/48 hours of technical grade No effect on carbon fixation was observed in mixed algae exposed to 1000 mcg/L/4 hours of technical grade No effect on shell growth was observed in Crassostrea virginica (oyster) exposed to 2000 mcg/L/96 hours of technical grade LD50 Mallard, oral, greater than 2000 mg/kg LD50 Pheasant, oral, 500 to 1000 mg/kg
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- 2,4,5-T is an odorless, colorless to white/tan, non-combustible, crystalline solid (HSDB, 2005; CHRIS , 1992; Budavari, 1989; ACGIH, 1986) .
- It has been described as having a metallic taste (Proctor et al, 1988).
PH
VAPOR PRESSURE
- 0 mmHg (at 20 degrees C) (ACGIH, 1986)
DENSITY
- OTHER TEMPERATURE AND/OR PRESSURE
FREEZING/MELTING POINT
BOILING POINT
FLASH POINT
EXPLOSIVE LIMITS
SOLUBILITY
2,4,5-T is soluble in alcohol (Budavari, 1989). Solubility in ethanol or isopropyl alcohol: 590 mg/kg (HSDB, 2005). It is very slightly soluble in petroleum ether (HSDB, 2005). Solubilities (in %) at 25 degrees C (HSDB, 2005): 95% Ethanol: 54.8 Ethyl ether: 23.4 n-Heptane: 0.039 Methanol: 49.60 Toluene: 0.73 Xylene: 0.61
HENRY'S CONSTANT
- 3.44x10(-8) atm-m(3)/mol (Ehrenfeld et al, 1986)
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