1,3,5-트라이메틸벤젠

Excerpt from ERG Guide 129 [Flammable Liquids (Water-Miscible / Noxious)]:

Use alcohol-resistant foam, dry powder, carbon dioxide. In case of fire: keep drums, etc., cool by spraying with water.

Fresh air, rest. Refer for medical attention.

Remove contaminated clothes. Rinse skin with plenty of water or shower.

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

Rinse mouth. Do NOT induce vomiting. Refer for medical attention .

· CALL 911. Then call emergency response telephone number on shipping paper. If shipping paper not available or no answer, refer to appropriate telephone number listed on the inside back cover.

· ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from immediate area.

Excerpt from NIOSH Pocket Guide for 1,3,5-Trimethylbenzene:

General First Aid:

(General first aid procedures)

· Wear positive pressure self-contained breathing apparatus (SCBA).

20.0 [ppm]

This chemical is a flammable liquid. Poisonous gases are produced in fire. Small fires: dry chemical, carbon dioxide, water spray, or alcohol foam. Large fires: water spray, fog, or alcohol foam. Move container from fire if you can do so without risk. Spray cooling water on containers that are exposed to flames until well after fire is out. For massive fire in cargo area, use unmanned hose holder or monitoring nozzles; if this is impossible, withdraw from area and let fire burn. Withdraw immediately in case of rising sound from venting safety device or any discoloration of tank due to fire. Isolate for one-half mile in all directions if tank car or truck is involved in fire. Vapors are heavier than air and will collect in low areas. Vapors may travel long distances to ignition sources and flashback. Vapors in confined areas may explode when exposed to fire. Containers may explode in fire. Storage containers and parts of containers may rocket great distances, in many directions. If material or contaminated runoff enters waterways, notify downstream users of potentially contaminated waters. Notify local health and fire officials and pollution control agencies. From a secure, explosion-proof location, use water spray to cool exposed containers. If cooling streams are ineffective (venting sound increases in volume and pitch, tank discolors, or shows any signs of deforming), withdraw immediately to a secure position. If employees are expected to fight fires, they must be trained and equipped in OSHA 1910.156.

If material on fire or involved in fire: Do not extinguish fire unless flow can be stopped or safely confined. Use water in flooding quantities as fog. Solid streams of water may be ineffective. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Use foam, dry chemical, or carbon dioxide. Keep run-off water out of sewers and water sources.

Prior to working with this chemical you should be trained on its proper handling and storage. This chemical must be stored to avoid contact with oxidizers (such as perchlorates, peroxides, permanganates, chlorates, and nitrates), and strong oxidizers (such as chlorine, bromine, and fluorine) since violent reactions occur. Store in tightly closed containers in a cool, well-ventilated area away from heat. Sources of ignition such as smoking and open flames are prohibited where this chemical is used, handled, or stored in a manner that could create a potential fire or explosion hazard. Metal containers involving the transfer of 5 gallons or more of this chemical should be grounded and bonded. Drums must be equipped with self-closing valves, pressure vacuum bungs, and flame arresters. Use only nonsparking tools and equipment, especially when opening and closing containers of this chemical.

STORAGE TANKS SHOULD BE MOUNDED TO CONFINE ESCAPING LIQUID & ESCAPE FROM PROCESS VESSELS SHOULD BE CONTROLLED IN SIMILAR MANNER BY SILLS @ DOORWAYS, DESIGN OF FLOORS, ETC. /TRIMETHYLBENZENES/

Evacuate and restrict persons not wearing protective equipment from area of spill or leak until cleanup is complete. Remove all ignition sources. Ventilate area of spill or leak. Absorb liquids in vermiculite, dry sand, earth, peat, carbon, or similar material and deposit in sealed containers. Keep this chemical out of a confined space ... because of the possibility of an explosion ... It may be necessary to contain and dispose of this chemical as a hazardous waste. If material or contaminated runoff enters waterways, notify downstream users of potentially contaminated waters. Contact your Department of Environmental Protection or your regional office of the federal EPA for specific recommendations. If employees are required to clean up spills, they must be properly trained and equipped. OSHA 1910.120(q) may be applicable.

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.

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

Environmental considerations-air spill: Apply water spray or mist to knock down vapors.

SRP: The most favorable course of action is to use an alternative chemical product with less inherent propensity for occupational exposure or environmental contamination. Recycle any unused portion of the material for its approved use or return it to the manufacturer or supplier. Ultimate disposal of the chemical must consider: the material's impact on air quality; potential migration in soil or water; effects on animal, aquatic, and plant life; and conformance with environmental and public health regulations.

Incineration /SRP: with appropriate emission controls/.

Personal protection: filter respirator for organic gases and vapours adapted to the airborne concentration of the substance. Do NOT wash away into sewer. 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.

5 of 46 human adipose tissue samples contained unreported concentrations of 1,3,5-trimethylbenzene(1). Expired air from 28 humans contained 1,3,5-trimethylbenzene at an average concn of 4 ng/L(2). Expired air from 54 humans contained 1,3,5-trimethylbenzene at an average concn of 0.842 ng/L(3). Expired air from 3 of 8 male humans contained 1,3,5-trimethylbenzene at 0.034 to 0.81 ug/hr; the source was thought to be of metabolic origin(4).

Increased catalase activity was observed in the liver microsomal fraction of ethanol-treated rats (10% v/v aqueous ethanol solution per os for 5 weeks). In contrast, cytochrome P-450 concentration and specific activity of NADPH-cytochrome c reductase remained at the same level as in the liver of control rats (drinking water). ... Administration of mesitylene (1,3,5-trimethylbenzene) by gastric tube for 3 days (5 mmoles per kg daily) increased cytochrome P-450 concentration, specific activity of NADPH-cytochrome c reductase and ethanol metabolism.

Groups of 5 female SPF Sprague-Dawley rats (200 to 220 g) were exposed via inhalation for 2 hr to 120, 180, 400, or 720 ppm mesitylene, without or in combination with 1000 or 4000 ppm ethyl acetate. Immediately after exposure, blood samples were collected. Co-exposure /of the effect/ with ethyl acetate ... was not statistically significant. For example, at 400 ppm mesitylene, control blood concn was (75.8 +/- 2.1) x 10-6 mol/L vs 68.8 +/ - 7.8) x 10-6 mol/L at 4000 ppm ethyl acetate.

Developmental

Eyes, skin, respiratory system, central nervous system, blood

EC50 Daphnia magna /(Water flea)/ 50 mg/L 24 hr, toxic effect: increased mortality and reduced reproduction rates

EC50; Species: Scenedesmus subspicatus (Green algae, Log growth phase); Conditions: freshwater, static, 24 °C, pH 8.0-9.3; Concentration: 25000 ug/L for 48 hr; Effect: decreased population biomass

EC50; Species: Scenedesmus subspicatus (Green algae, Log growth phase); Conditions: freshwater, static, 24 °C, pH 8.0-9.3; Concentration: 53000 ug/L for 48 hr; Effect: general population changes

EC50; Species: Daphnia magna (Water flea, age 4-6 days, length 1.5 mm); Conditions: freshwater, static, 23 °C, pH 6-7, dissolved oxygen 5-9 mg/L; Concentration: 50 mmol/cu m for 48 hr (95% confidence interval: 22-110 mmol/cu m); Effect: intoxication, immobilization /> or = 97% purity/

For more Ecotoxicity Values (Complete) data for 1,3,5-TRIMETHYLBENZENE (9 total), please visit the HSDB record page.

TERRESTRIAL FATE: Based on a classification scheme(1), an experimental Koc range of 501-1,445(2-5), indicates that 1,3,5-trimethylbenzene is expected to have low mobility in soil(SRC). Volatilization of 1,3,5-trimethylbenzene from moist soil surfaces is expected to be an important fate process(SRC) given an experimental Henry's Law constant of 8.77X10-3 atm-cu m/mole(6). 1,3,5-Trimethylbenzene is expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 2.48 mm Hg(SRC), from experimentally-derived coefficients(7). Complete removal of 1,3,5-trimethylbenzene from sterile sandy loam soil samples contaminated with jet fuel was reported within 5 days, probably due to evaporation(8). Biodegradation is expected to occur in soil, and acclimation may increase the rate of biodegradation(SRC). 1,3,5-Trimethylbenzene, present at a concn of 50 mg/kg, degraded considerably after 6 months in the presence of a sewage inoculum during a bioremediation study(9). It was noted that 1,3,5-trimethylbenzene was more resistant to biodegradation than other compounds present(9). The time required for 0.2-1.0 mg/L of 1,3,5-trimethylbenzene to reach less than 1 ug/L was 110 hours in an adapted groundwater aquifer contaminated with gasoline(10).

AQUATIC FATE: Based on a classification scheme(1), an experimental Koc range of 501-1,445(2-5), indicates that 1,3,5-trimethylbenzene is expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected based upon a Henry's Law constant of 8.77X10-3 atm-cu m/mole(6). Using this Henry's Law constant and an estimation method(7), volatilization half-lives for a model river and model lake are 1.2 hours and 4.4 days, respectively(SRC). Residence times (with respect to volatilization) for 1,3,5-trimethylbenzene were calculated as 220 hours for both winter and summer conditions in Narragansett Bay(8). According to a classification scheme(9), BCF values of 23 to 342(10), measured in carp, suggest that bioconcentration in aquatic organisms may be high(SRC). Biodegradation may be an important fate process for this compound in water, and acclimation may increase the rate of biodegradation(SRC). The time required for 0.2-1.0 mg/L of 1,3,5-trimethylbenzene to reach less than 1 ug/L was 110 hours in an adapted groundwater aquifer contaminated with gasoline(11). 1,3,5-Trimethylbenzene was not detected in the effluent of an activated sludge plant that had a recorded influent of 22.7 ug/L(12). In liquid wastewater cultures, after 30 days 1,3,5-trimethylbenzene degraded to 0.39 mg/L in the test sample compared to 7.17 mg/L residual concn in the abiotic control, suggesting biodegradation is an important fate process in water(13).

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), 1,3,5-trimethylbenzene, which has a vapor pressure of 2.48 mm Hg at 25 °C(2), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase 1,3,5-trimethylbenzene 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 11 hours(SRC), calculated from its rate constant of 5.75X10-11 cu cm/molecule-sec at 25 °C(1). 1,3,5-Trimethylbenzene also reacts with nitrate radicals in the atmosphere(3); the half-life for this reaction in air is estimated as 10-67 days(SRC). The photooxidation of 1,3,5-trimethylbenzene with nitrogen oxide produces formaldehyde and aliphatic aldehydes at 0.15-0.2 and 0.3-0.4 moles/mole 1,3,5-trimethylbenzene, respectively(5). 1,3,5-Trimethylbenzene does not contain chromophores that absorb wavelengths >290 nm(6) and therefore is not expected to be susceptible to direct photolysis by sunlight(SRC).

An aroma concentrate of cured beef contained 1,3,5-trimethylbenzene at 0.11 mg/kg(1). 1,3,5-Trimethylbenzene was reported as a component of fried beef liver (4.34-5.57 ppb)(2), margarine (13.1 ppb)(2), butter (7.81 ppb)(2), cake doughnuts (27.6 ppb)(2), sandwich cookies (7.25 ppb)(2), in scrambled eggs from both fresh and supermarket eggs (trace levels)(3), and chickpea seed(4). 1,3,5-Trimethylbenzene is a volatile component of chicken, beef, and pork flavors(5).

The substance can be absorbed into the body by inhalation.

inhalation, ingestion, skin and/or eye contact

Confusion. Cough. Dizziness. Drowsiness. Headache. Sore throat. Vomiting.

Redness. Dry skin.

Redness. Pain.

See Inhalation.

irritation eyes, skin, nose, throat, respiratory system; bronchitis; hypochromic anemia; headache, drowsiness, lassitude (weakness, exhaustion), dizziness, nausea, incoordination; vomiting, confusion; chemical pneumonitis (aspiration liquid)

Diluted (30:1 with purified air) automobile exhaust contained 2.3 ppm 1,3,5-trimethylbenzene(1). Automobile exhaust from an English car without a catalytic converter contained 1,3,5-trimethylbenzene at 1242 ppb(2). Highway tunnel exhaust air in Hamburg, Germany (Elbtunnel) contained 1,3,5-trimethylbenzene at concns from 14.2 to 18.2 ug/cu m(3). Gasoline engine exhaust from a light-duty vehicle both with and without a catalytic converter contained 1,3,5-trimethylbenzene at 1.3 and 0.6 wt% of total organic gas emissions, respectively(4). Unburned gasoline in the summertime contained 1.2 wt% 1,3,5-trimethylbenzene(4). 1,3,5-Trimethylbenzene was introduced into water at 10 mg/10 minutes by a four-stroke outboard motor(5). The concn of 1,3,5-trimethylbenzene in the water of a canal to a harbor of Lake Constance, Germany, varied throughout the day with 7, 23, 159, 72, 233, 233, 233, and 267 ng/L reported for times 8:30, 9:37, 10:37, 11:40, 12:42, 15:20, 16:20, and 17:30, respectively(6). Emissions from a municipal waste incineration plant contained 1,3,5-trimethylbenzene at 0.34 ug/cu m(7). 1,3,5-Trimethylbenzene was reported as one of the 99 most frequently detected compounds at Superfund sites(8).

1,3,5-Trimethylbenzene was detected in leachate samples from 6 of 6 hazardous waste landfills at concns from 10 to 1380 ug/L and in 4 of 5 leachate samples from domestic landfills at concns of 2.6 to 4.8 ug/L(1). Influent to the Jones Island publicly-owned treatment plant contained 1,3,5-trimethylbenzene at 7 to 14 ppb; effluent contained less than 1 ppb(2). Effluent samples from an in situ coal gasification experiment in Hanna, WY contained 1,3,5-trimethylbenzene from not detected (detection limit=0.1 ppb) to 139 ppb(3). Dissolved air flotation treatment effluent from a class B petroleum refinery contained 1,3,5-trimethylbenzene at43 ng/g(4). Three of six mixed household waste samples contained 1,3,5-trimethylbenzene at unreported concns(5). 1,3,5-Trimethylbenzene was tentatively identified in leachate from the North Bay, Ontario landfill(6). Emissions from coal-fired power stations in France contained 1,3,5-trimethylbenzene at 0.7 to 7.1 ug/Normalized cu m(7). 1,3,5-Trimethylbenzene was detected in leachate samples from 6 of 6 hazardous waste landfills at concns from 10 to 1380 ug/L and in 5 of 5 leachate samples from domestic landfills at concns of 2.6 to 4.8 ug/L(8).

Off-gas from two Ontario municipal wastewater treatment plants, Skyway in Burlington and Highland Creek in Metropolitan Toronto, Canada contained 1,3,5-trimethylbenzene at maximum concns of 271 and 1090 ug/cu m, respectively; emission rates of 32 and 138 g/d were estimated(1). Effluent samples collected from advanced waste treatment plants in Lake Tahoe, CA (in (1974), Pomona, CA (in 1974/1975) and Blue Plains facility, Washington DC (in 1974) contained 1,3,5-trimethylbenzene at unreported concns(2). Emissions from municipal solid waste composting facilities contained 1,3,5-trimethylbenzene at concns of 320, 130, 46, and 7 ug/cu m for fresh, mid-aged, old, and curing compost, respectively(3). Wastewater from the following industries contained unreported concns of 1,3,5-trimethylbenzene: petroleum refining, paint andink, ore mining, inorganic chemicals, textile mills, auto and other laundries, plastics manufacturing, electronics, and publicly-owned treatment works(4).

Pursuant to section 8(d) of TSCA, EPA promulgated a model Health and Safety Data Reporting Rule. The section 8(d) model rule requires manufacturers, importers, and processors of listed chemical substances and mixtures to submit to EPA copies and lists of unpublished health and safety studies. 1,3,5-Trimethylbenzene is included on this list. Effective date: 2/13/1984; Sunset date: 2/13/1994.

A testing consent order is in effect for 1,3,5-trimethylbenzene for health effects testing. FR citation: FR 59681 11/10/1993.

(CA) CALIFORNIA 330 ug/l

(CT) CONNECTICUT 36 ug/l

(FL) FLORIDA 35 ug/l

(MN) MINNESOTA 100 ug/L

(NH) NEW HAMPSHIRE 330 ug/L

Found in coal tar and petroleum crudes; [Merck Index] Used to make dyes and UV oxidation stabilizers for plastics; Also used as a solvent and paint thinner; [HSDB]

Painting (Solvents) [Category: Paint]

DYESTUFF INTERMEDIATE, SOLVENT, PAINT THINNER

Chem int for anthraquinone vat dyes and for uv oxidation stabilizers for plastics

Used as a chemical intermediate for the synthesis of mesidine; trimesic acid; 2,4,6-tris(3,5-di-t-butyl-4-hydroxybenzyl)mesitylene.

The principal use for mesitylene is its conversion to 1,3,5-trimethyl-2,4,6-tris(3,5-di-tert-butyl-4-hydroxybenzyl)benzene; trade name is Ethanox 330 ... an important non-coloring stabilizer (antioxidant) for plastics, adhesives, rubber, and waxes.

(1972) No Data

(1975) No Data

(1984) 1.58X10+8 g

2023: 850,000 - <1,000,000 lb

(1972) PROBABLY GREATER THAN 4.54X10+5 GRAMS

(1975) PROBABLY GREATER THAN 4.54X10+5 GRAMS

(1986) No Data

1,3,5-Trimethylbenzene is listed as a High Production Volume (HPV) chemical (65FR81686). Chemicals listed as HPV were produced in or imported into the U.S. in >1 million pounds in 1990 and/or 1994. The HPV list is based on the 1990 Inventory Update Rule. (IUR) (40 CFR part 710 subpart B; 51FR21438).

Production volumes for non-confidential chemicals reported under the Inventory Update Rule. [Table#269]

BY DEHYDRATING ACETONE WITH SULFURIC ACID.

Trimethylbenzene fraction (fractionation; coproduced with pseudocumene/durene)

Acetone undergoes aldol addition in the presence of sulfuric acid to give mesityl oxide, which then condenses with a third molecule of acetone to give a mixture of phorone (2,6-dimethyl-2,6-heptadien-4-one) and mesitylene (1,3,5-trimethylbenzene).

During the KOCH process, pure pseudocumene or a recycle mixture of polymethylbenzenes having an average molecular weight of 120 (C9 PMB) is contacted with a strong Friedel-Crafts catalyst, disproportionation occurs. At 127 °C, the reactor effluent contains approximately 3% toluene, 21% xylenes, 44% C9 PMBs, 29% C10 PMBs, and 3% pentamethylbenzene...Based on the values at 127 °C, the distribution is 29.5% mesitylene, 66.0% pseudocumene, and 4.5% hemimellitene. Mesitylene and hemimellitene are separated by fractionation....

For more Methods of Manufacturing (Complete) data for 1,3,5-TRIMETHYLBENZENE (6 total), please visit the HSDB record page.

Cosmetics product ingredient: 1,3,5-Trimethylbenzene (Mesitylene)

Information on 66 consumer products that contain Mesitylene (1,3,5-Trimethylbenzene) in the following categories is provided:

Transportation Equipment Manufacturing

Benzene, 1,3,5-trimethyl-: ACTIVE

High purity mesitylene is produced synthetically.