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Chemical Fact Sheet

Chemical Abstract Number (CAS #) 606202
Synonyms2,6-Dinitrotoluene
Benzene, 2-methyl-1,3-dinitro-
2,6-DNT
Analytical Methods EPA Method 609
EPA Method 625
EPA Method 8250A
Molecular FormulaC7H6N2O4
Use CHEM INT FOR TOLUENE-2,6-DIAMINE, A TOLUENE DIISOCYANATE INT; GELATINIZING & WATERPROOFING AGENT IN EXPLOSIVES Used in the synthesis of TNT, urethane polymers, flexible and rigid foams, surface coatings and dyes
Apparent Color RHOMBIC NEEDLES FROM ALCOHOL; Yellow to red solid
Odor Slight odor
Boiling Point 285 deg C
Melting Point 66 DEG C
Density 1.2833 @ 111 DEG C
Sensitivity Data Immediately irritating to the eye.
Environmental Impact Recent information indicated that two companies produced 2,6-dinitrotoluene (2,6-DNT) as a mixture with 2,4-DNT. No specific use information was found for 2,6-DNT; however, dinitrotoluenes are used in organic synthesis, dyes, and explosives and probably some of it is consumed in isocyanate production along with 2,4-DNT. Information on the routes and amounts of 2,6-DNT released to the environment was not found; however, 2,6-DNT may enter the environment from its production and use. If released to soil, 2,6-DNT is expected to biodegrade. It should be fairly mobile, based on experiments in sandy loam and sandy slit loam soil. If released to water, 2,6-DNT will readily biodegrade. Photooxidation should be rapid in surface layers of water. 2,6-DNT should not adsorb appreciably to sediments or suspended solids. Volatilization from water or soil will not be significant. In the atmosphere, 2,6-DNT will not react with photochemically produce hydroxyl radicals. Its half-life is estimated to be 47 days. Exposure to 2,6-DNT will primarily be occupational via dermal contact.
Environmental Fate TERRESTRIAL FATE: If released in soil, 2,6-DNT would be expected to readily biodegrade. 2,6-DNT's half-life in two soils was 73 and 92 days . The calculated soil adsorption coefficient (KOC = 204 ) for 2,6-dinitrotoluene (2,6-DNT) and an estimated log KOW of 1.72 indicates that 2,6-DNT is slightly mobile in soil(3,SRC). However, experimental data with 2,6-DNT in two soils indicates that its adsorptivity to soil is much lower . Due to its very low vapor pressure, volatilization from the soil surface should be negligible(5,SRC). Aromatic nitro compounds are not susceptible to hydrolysis . AQUATIC FATE: 2,6-DNT readily degrades in both river water and sea water and this would be expected to be the most significant fate process in the aquatic environment(6-8). The estimated log Koc for 2,6-DNT(1,3) and experimental adsorption data, suggests that 2,6-DNT will have a slight tendency to sorb to sediments, suspended solids and biota. Volatilization from rivers and lakes will not be significant based on calculations using an estimated Henry's Law constant(3-4). The half-life for 2,6-DNT in river water exposed to sunlight was 12 minutes and was determined to be an indirect photoreaction . Thus, photolysis may be a removal mechanism for 2,6-DNT in surface layers of water. ATMOSPHERIC FATE: 2,6-DNT degrades by reaction with photochemically produced hyroxyl radicals in the atmosphere. Its half-life is estimated to be 47 days(1,SRC).
Drinking Water Impact SEAWATER: 2,6-Dinitrotoluene was found in Dokai Bay, Japan at concentrations up to 14.8 ug/l . DRINKING WATER: 2,6-Dinitrotoluene was found in drinking water at an unspecified location at an unspecified concentration . SURFACE WATER: 2,6-Dinitrotoluene concns of 4.1 and 7.6 ug/L were detected in surface water samples collected from two brooks near Hirschagen/Waldhof, Germany in the vicinity of munitions manufacture during World War II ; the river into which the brooks feed (River Losse) had a concn of 0.1 ug/L ; two ponds in manufacture) had levles of 0.3 and 0.07 ug/L ; the ponds feed into the River Oder which had a level of 0.02 ug/L . EFFL: 2,6-Dinitrotoluene (2,6-DNT) concentration in raw wastewater from a textile plant was 50 mg/cu m and was an average of 4.3 mg/l in the wastewater from 2,4,6-trinitrotoluene production .

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