Sunlight irradiation induces formation of reactive oxygen
species (superoxide, hydroperoxyl radical, singlet oxygen, etc.),
which readily take part in degradation of environmental pollutants.
Being a primary ingredient in a suite of insensitive munition formulations,
NTO (5-nitro-1,2,4-triazol-3-one) can be released onto training range
soils and reduced to ATO (5-amino-1,2,4-triazol-3-one) by soil bacteria
or iron-contained minerals. ATO can be dissolved in surface water
and groundwater due to its good water solubility and then undergo
further decomposition. A detailed investigation of possible mechanisms
for ATO decomposition in water induced by superoxide, hydroperoxyl
radical, and singlet oxygen as pathways for ATO environmental degradation
was performed by computational study at the PCM(Pauling)/M06-2X/6-311++G(d,p) level. Hydrolysis and degradation of ATO
induced by superoxide are unlikely to occur due to the high activation
energy or endergonicity of the processes. The hydroperoxyl radical
causes rapid and reversible hydrogen transfer from ATO, while an attachment
of the hydroperoxyl radical to ATO can induce decomposition of ATO,
leading to its mineralization. Singlet oxygen shows a higher reactivity
toward ATO than the hydroperoxyl radical. Decomposition of ATO was
found to be a multistep process that begins with singlet oxygen attachment
to the carbon atom of the CN double bond. The intermediate
that is formed undergoes recyclization, cycle opening, and sequential
elimination of nitrogen gas, ammonia, and carbon(IV) oxide. Isocyanic
acid, which arises intermediately, hydrolyzes into ammonia and carbon(IV)
oxide. Calculated activation energies and high exergonicity of the
studied processes support the contribution of singlet oxygen and the
hydroperoxyl radical to ATO degradation into low-weight inorganic
compounds in the environment.