Table 4.
Byproducts/end-products of HMX degradation via different treatment approaches.
Treatment Approach | HMX Degradation Byproducts (Intermediate/End-Products) | References |
---|---|---|
Biodegradation of HMX by Planomicrobium flavidum | NO2−, methylenedintramine, and N-methyl-N,N′-dinitromethanediamine |
[4] |
Alkaline hydrolysis | NO2−, N2O, NH3, N2, and HCOOH | [1] |
Bioaugmentation using Janibacter cremeus, an immobilized mixture of calcite and cocopeat for bioaugmentation. | Nitroso derivatives (5-hydroxy-4-nitro-2,4-diazapentanal and NDAB (further breaks down to HCHO) | [8] |
Biodegradation by sediment microorganisms | Mononitroso derivatives | [85] |
Degradation by TiO2 photocatalysis | NO3−, NO2−, and NH4+ | [38] |
Reduction by nZVI | Formaldehyde/methanol/hydrazine/dimethyl hydrazine | [40] |
Electro-assisted Fenton treatment of HMX | HCOOH, NO3−, NH4+, andCO2 | [25] |
Biodegradation under the mixed electron-acceptor condition | Under mixed electron-acceptor conditions, the major metabolites were CHCl3 and CH3OH. Under methanogenic, fermenting, sulfate, and nitrate-reducing conditions, mono-, di-, and tri-nitroso derivatives were produced from HMX | [7] |
Fenton oxidation | NO3− and N2 | [30] |
Xanthine oxidase catalyzed biotransformation | NO2−, methylenedinitramine (MDNA), 4-nitro-2,4-diazabutanal (NDAB), HCHO, N2O, HCOOH), and NH4+ | [9] |
Nitrite and nitrate | NO2− and NO3− | [31] |
Photocatalytic degradation | NO2−, NO3−, and NH4+ | [43] |
Reduction by zero-valent Iron | HCHO, NH4+, N2O, and NH2NH2 | [29] |