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Move the victim into fresh air. If breathing is difficult, give oxygen. If not breathing, give artificial respiration and consult a doctor immediately. Do not use mouth to mouth resuscitation if the victim ingested or inhaled the chemical.
Take off contaminated clothing immediately. Wash off with soap and plenty of water. Consult a doctor.
Rinse with pure water for at least 15 minutes. Consult a doctor.
Rinse mouth with water. Do not induce vomiting. Never give anything by mouth to an unconscious person. Call a doctor or Poison Control Center immediately.
SYMPTOMS: Symptoms of exposure to this compound may include skin and eye irritation. ACUTE/CHRONIC HAZARDS: This compound may cause irritation on contact. When heated to decomposition it emits toxic fumes. (NTP, 1992)
The chlorophenoxy compounds are absorbed across the gut wall, lung, & the skin. they are not significantly fat storable. excretion occurs within hours, or at most days, primarily in the urine. chlorophenoxy cmpd
Extinguish fire using agent suitable for type of surrounding fire. 2,4,5-T amine, ester, or salt
Flash point data for this chemical are not available. It is probably combustible. (NTP, 1992)
Wear self-contained breathing apparatus for firefighting if necessary.
Avoid dust formation. Avoid breathing mist, gas or vapours.Avoid contacting with skin and eye. Use personal protective equipment.Wear chemical impermeable gloves. Ensure adequate ventilation.Remove all sources of ignition. Evacuate personnel to safe areas.Keep people away from and upwind of spill/leak.
Prevent further spillage or leakage if it is safe to do so. Do not let the chemical enter drains. Discharge into the environment must be avoided.
Land spill: Dig a pit, pond, lagoon, holding area to contain liquid or solid material. /SRP: If time permits, pits, ponds, lagoons, soak holes, or holding areas should be sealed with an impermeable flexible membrane liner./ Cover solids with a plastic sheet to prevent dissolving in rain or fire fighting water. 2,4,5-T amine, ester, or salt
Handling in a well ventilated place. Wear suitable protective clothing. Avoid contact with skin and eyes. Avoid formation of dust and aerosols. Use non-sparking tools. Prevent fire caused by electrostatic discharge steam.
Store the container tightly closed in a dry, cool and well-ventilated place. Store apart from foodstuff containers or incompatible materials.
no data available
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Ensure adequate ventilation. Handle in accordance with good industrial hygiene and safety practice. Set up emergency exits and the risk-elimination area.
Wear tightly fitting safety goggles with side-shields conforming to EN 166(EU) or NIOSH (US).
Wear fire/flame resistant and impervious clothing. Handle with gloves. Gloves must be inspected prior to use. Wash and dry hands. The selected protective gloves have to satisfy the specifications of EU Directive 89/686/EEC and the standard EN 374 derived from it.
If the exposure limits are exceeded, irritation or other symptoms are experienced, use a full-face respirator.
no data available
PHYSICAL DESCRIPTION: Clear colorless liquid or white solid. (NTP, 1992)
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82 to 86° F (NTP, 1992)
371.9°C at 760 mmHg
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142.2°C
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less than 1 mg/mL at 70° F (NTP, 1992)
log Kow= 4.81.
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1.324g/cm3
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They will burn, though they may take some effort to ignite. /2,4,5-T amine, ester, or salt/2,4,5-T, N-BUTYL ESTER is an ester of a chlorinated organic acid. May react exothermically with acids to generate butyl alcohol and 2,4,5-trichlorophenoxyacetic. Strong oxidizing acids may cause a reaction that is sufficiently exothermic to ignite the reaction products. Heat may also be generated with caustic solutions.
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Hydrogen chloride gas and other irritating fumes may form during fires. 2,4,5-T esters
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Classification of carcinogenicity: 1) evidence in humans: limited; Overall summary evaluation of carcinogenic risk to humans is Group 2B: The agent is possibly carcinogenic to humans. Chlorophenoxy herbicides; From table
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No data on the bioconcentration of the n-butyl ester of 2,4,5-T could be found in the literature. From the log of its octanol/water partition coefficient, 4.8(1), one would estimate a log BCF of 3.43(2). Because of hydrolysis, this bioconcentration potential must be viewed as an upper limit(SRC).
Concentrations of 2,4-D and 2,4,5-T in soils and leachates ... were monitored for up to 28 months to characterize the patterns of herbicide mobility in soils under climatic conditions of the Palouse region of the Pacific Northwest (USA). ... Soils from Washington, Wyoming, or Mississippi ... treated with 1120 or 5600 kg/ha of a 1:1 mixture of 2,4-D and 2,4,5-T n-butyl esters in 1976, 1977, or 1978. The winter of 1976-1977 was mild and relatively dry, and little leachate could be collected. Subsequent winters were wet and the soil columns were saturated by the following springs. 2,4-D (< 1 ppm) was found in leachates from Washington and Wyoming soils receiving the herbicide application in 1976 or 1977 and > 30 ppm was found in leachates from Washington soil treated in 1978. 2,4-D (> 10 ppm) was found in leachates from the acidic Mississippi soil receiving high rate of herbicide application in 1977 or 1978. Concentrations of 2,4,5-T in the same leachates were higher for the Washington and Wyoming soils, but lower (than corresponding concentrations of 2,4-D) for the Mississippi soil. In all cases, 96-99% of the undegraded herbicides ... remained in the 0-10 cm soil layer after 2-3 winters, and only 0.14-1.65% of the 2,4,-D and 0.33-3.7% of the 2,4,5-T remaining ... were present in the 10-30 cm depths. Mobility characterization by soil TLC showed that the ester form of both herbicides was relatively immobile, the acid form was less mobile in the Mississippi soil than in Washington and Wyoming soils and 2,4-D was slightly more mobile than 2,4,5-T under corresponding conditions.
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The material can be disposed of by removal to a licensed chemical destruction plant or by controlled incineration with flue gas scrubbing. Do not contaminate water, foodstuffs, feed or seed by storage or disposal. Do not discharge to sewer systems.
Containers can be triply rinsed (or equivalent) and offered for recycling or reconditioning. Alternatively, the packaging can be punctured to make it unusable for other purposes and then be disposed of in a sanitary landfill. Controlled incineration with flue gas scrubbing is possible for combustible packaging materials.
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: No
IMDG: No
IATA: No
no data available
no data available