Microbial 2,4,6-trinitrotoluene degradation: could we learn from (bio)chemistry for bioremediation and vice versa?

2,4,6-Trinitrotoluene (TNT) is released in nature from manufacturing or demilitarization facilities but also after munitions firing/detonation or leakage from explosive remnants of war. Due to its toxicity and recalcitrance, life cycle of TNT-containing products and bioremediation are critical issues. As TNT is a strongly electron-deficient aromatic with a positive molecular quadrupole moment and three electrophilic nitro groups, its environmental fate is contingent upon specific sorptive electron donor-acceptor interactions and nucleophilic, reductive (bio)transformations. The microbial degradation of TNT is governed by cometabolism and therefore depends on the growth substrate(s) available in contaminated environments. Long considered an ecotoxicological safety endpoint, the immobilization of TNT metabolites derived from nitro moiety reduction in soil is controversial because they preferentially bind to the dissolved soil organic matter which can be released into surface and groundwaters. The ever-growing biochemical knowledge of TNT degradation has made bioaugmentation and phytoremediation attractive alternatives. While the discovery and engineering of microorganisms with novel/improved degradative abilities are very challenging, the deciphering of the physiological roles of promiscuous enzymes involved in TNT biodegradation, such as type II hydride transferases of the Old Yellow Enzyme family, opens new perspectives for bioremediation. Finally, transgenic plants have enabled effective phytoremediation at the field scale, which is emerging as the preferable in situ option to rehabilitate TNT-contaminated sites.