2,4-Dimethylaniline

Fires involving this material can be controlled with a dry chemical, carbon dioxide or Halon extinguisher. (NTP, 1992)

Use water spray, carbon dioxide, foam, powder.

Fresh air, rest. Refer for medical attention.

Remove contaminated clothes. Rinse and then wash skin with water and soap. Refer for medical attention .

First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.

Rinse mouth. Refer for medical attention .

EYES: First check the victim for contact lenses and remove if present. Flush victim's eyes with water or normal saline solution for 20 to 30 minutes while simultaneously calling a hospital or poison control center. Do not put any ointments, oils, or medication in the victim's eyes without specific instructions from a physician. IMMEDIATELY transport the victim after flushing eyes to a hospital even if no symptoms (such as redness or irritation) develop.

Use water spray, dry chemical, foam, or CO2. Wear full protective clothing. /Xylidines/

If material on fire or involved in fire: Extinguish fire using agent suitable for type of surrounding fire. (Material itself does not burn or burns with difficulty.) Use water in flooding quantities as fog. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. /Xylidines/

Environmental considerations - 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./ Dike surface flow using soil, sand bags, foamed polyurethane, or foamed concrete. Absorb bulk liquid with fly ash, cement powder, or commercial sorbents. /Xylidines/

Environmental considerations - water spill: Use natural barriers or oil spill control booms to limit spill travel. Remove trapped material with suction hoses. /Xylidines/

SMALL SPILLS AND LEAKAGE: If you spill this chemical, FIRST REMOVE ALL SOURCES OF IGNITION. Then, use absorbent paper to pick up all liquid spill material. Your contaminated clothing and absorbent paper should be sealed in a vapor-tight plastic bag for eventual disposal. Solvent wash all contaminated surfaces with 60-70% ethanol followed by washing with a soap and water solution. Do not reenter the contaminated area until the Safety Officer (or other responsible person) has verified that the area has been properly cleaned.

SRP: At the time of 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.

Disposal methods: incineration. A). Dissolve in such combustible solvent as alcohols, benzene, etc. Spray solvent into the furnace with afterburner and scrubber. B). Pour into a mixture of sand and soda ash (9:1). After mixing, put into a paper carton stuffed full with packing paper to serve as fuel. Burn in the furnace. /Xylidines/

Personal protection: chemical protection suit and filter respirator for organic gases and vapours adapted to the airborne concentration of the substance. Do NOT let this chemical enter the environment. Collect leaking and spilled liquid in sealable containers as far as possible. Absorb remaining liquid in sand or inert absorbent. Then store and dispose of according to local regulations.

SRP: The scientific literature for the use of contact lenses in industry is conflicting. The benefit or detrimental effects of wearing contact lenses depend not only upon the substance, but also on factors including the form of the substance, characteristics and duration of the exposure, the uses of other eye protection equipment, and the hygiene of the lenses. However, there may be individual substances whose irritating or corrosive properties are such that the wearing of contact lenses would be harmful to the eye. In those specific cases, contact lenses should not be worn. In any event, the usual eye protection equipment should be worn even when contact lenses are in place.

Non-impervious clothing which becomes contaminated with xylidine should be removed immediately and not reworn until the xylidine is removed from the clothing. /Xylidines/

Eating and smoking should not be permitted in areas where liquid xylidine is handled, processed, or stored. /Xylidines/

Employees who handle liquid xylidine should wash their hands thoroughly with soap or mild detergent and water before eating, smoking, or using toilet facilities. /Xylidines/

For more Preventive Measures (Complete) data for 2,4-XYLIDINE (7 total), please visit the HSDB record page.

TERRESTRIAL FATE: Based on a recommended classification scheme(1), an estimated Koc value of 200(SRC), determined from a measured log Kow of 1.68(2) and a recommended regression-derived equation(3), indicates that 2,4-xylidine will have moderate mobility in soil(SRC). However, anilines are expected to bind strongly to humus or soil organic matter in soils due to the high reactivity of the aromatic amino group(4,5), suggesting that mobility may be much lower in some soils with high organic carbon contents(SRC). Volatilization of 2,4-xylidine may be important from moist soil surfaces(SRC) given an estimated Henry's Law constant of 2.5X10-6 atm-cu m/mole(SRC), using a fragment constant estimation method(6). Based on limited data, 2,4-xylidine may biodegrade under aerobic conditions in soil(SRC); 2,4-xylidine was completely biodegraded in soil cultures within 2 days(7), and reached 36% degradation in 6 hours in an aqueous screening study using an activated sludge inoculum(8). However, it was classified as slow to biodegrade in the Japanese MITI test(9).

AQUATIC FATE: Based on a recommended classification scheme for soil(1), an estimated Koc value of 200(SRC), determined from a measured log Kow of 1.68(2) and a recommended regression-derived equation(3), suggests that 2,4-xylidine should not adsorb to suspended solids and sediment in water(SRC). However, aromatic amine groups are recognized as having a strong affinity to organic carbon, suggesting that this compound may bind strongly to suspended organic material in water(4,5). 2,4-Xylidine may volatilize from water surfaces(3,SRC) based on an estimated Henry's Law constant of 2.5X10-6 atm-cu m/mole(SRC), developed using a fragment constant estimation method(6). Estimated volatilization half-lives for a model river and model lake are 16 and 120 days, respectively(3,SRC), although adsorption to organic material may attenuate this process(SRC). According to a classification scheme(7), an estimated BCF value of 11(3,SRC), from a measured log Kow(2), suggests that bioconcentration in aquatic organisms is low(SRC). Based on limited data, 2,4-xylidine may rapidly biodegrade under aerobic conditions in water(SRC); 2,4-xylidine was completely biodegraded in soil cultures within 2 days(8) and reached 36% degradation in 6 hours in an aqueous screening study using an activated sludge inoculum(9). However, it was classified as slow to biodegrade in the Japanese MITI test(10). As a class, aromatic amines react relatively rapidly in sunlit natural water via reaction with photochemically-produced hydroxyl radicals and peroxy radicals(11); typical half-lives for peroxy and hydroxy radical reactions are on the order of 19 and 30 sunlight hours, respectively(11).

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), 2,4-xylidine, which has a measured vapor pressure of 0.133 mm Hg at 25 °C(2), should exist solely as a vapor in the ambient atmosphere. Vapor-phase 2,4-xylidine is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC); the half-life for this reaction in air is estimated to be about 2 hours(3,SRC).

Dizziness. Drowsiness. Headache. Nausea.

MAY BE ABSORBED! Redness. See Ingestion.

Redness. Pain.

Blue lips, fingernails and skin. Dizziness. Drowsiness. Headache. Nausea. Unconsciousness.

Initial medical examination: a complete history & physical examination. The purpose is to detect existing conditions that might place the exposed employee at increased risk, and to establish a baseline for future health monitoring. Exam of the blood, lungs, liver, kidneys, and cardiovascular system should be stressed. ... Periodic medical exam ... should be repeated on an annual basis. /Xylidine/

The Koc of 2,4-xylidine is estimated as approximately 200(SRC), using a measured log Kow of 1.68(1) and a regression-derived equation(2,SRC). According to a recommended classification scheme(3), this estimated Koc value suggests that 2,4-xylidine has moderate mobility in soil(SRC). However, adsorption to soil due to the high reactivity of the aromatic amino group to humus or soil organic matter rather than to clay particles may cause decreased mobility of this compound(4,5). Low adsorption is observed at a neutral pH with pure clay minerals or soils for substituted anilines(5).

2,4-Xylidine, incubated in chernozem soil at 500 ppm/kg, was biodegraded within 2 days; its transformation product was stable for >90 days(1). 2,4-Xylidine, initially present at 20 mg/l, was degraded by 36% in 6 hours using an activated sludge inoculum under aerobic conditions(2). In the Japanese MITI test, 2,4-xylidine (present at 100 mg/l) was classified as slow to biodegrade indicating that only 0-29% of the theoretical BOD was reached in 2 weeks using an activated sludge inoculum(3).

2,4-Xylidine

Group 3: Not classifiable as to its carcinogenicity to humans

Volume 16: (1978) Some Aromatic Amines and Related Nitro Compounds – Hair Dyes, Colouring Agents and Miscellaneous Industrial Chemicals

1987

1987

An estimated BCF value of 11 was calculated for 2,4-xylidine(SRC), using a measured log Kow of 1.68(1) and a recommended regression-derived equation(2). According to a classification scheme(3), this BCF value suggests that bioconcentration in aquatic organisms is low(SRC).