Hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) Biodegradation in Liquid and Solid-State Matrices by Phanerochaete chrysosporium

• Published in: Bioremediation journal 2001, Vol.5 (1), p.13-25
• Main Authors: Stahl, James D., Aken, Benoît Van, Cameron, Michael D., Aust, Steven D.
• Format: Article
• Language: English
• Subjects: Biodegradation of pollutants; Biological and medical sciences; Biotechnology; cyclonite; Environment and pollution; Fundamental and applied biological sciences. Psychology; hexahydro-1,3,5-trinitro-1,3,5-triazine; Industrial applications and implications. Economical aspects; Phanerochaete chrysosporium
• ISSN: 1088-9868; 1547-6529
• DOI: 10.1080/20018891079177

Extensive biodegradation of hexahydro-1,3,5 -trinitro-1,3,5 -triazine (RDX) by the white-rot fungus Phanerochaete chrysosporium in liquid and solid matrices was observed. Some degradation in liquid occurred under nonligninolytic conditions, but was approximately 10 times higher under ligninolytic conditions. Moreover, elimination was accounted for almost completely as carbon dioxide. No RDX metabolites were detected. The degradation rates in liquid appeared to be limited to RDX concentration in solution (approximately 80 mg/L), but degradation rates in soil were nonsaturable to 250 mg/kg. Manganese-dependent peroxidase (MnP) and cellobiose dehydrogenase (CDH) from P. chrysosporium, but not lignin peroxidase, were able to degrade RDX. MnP degradation of RDX required addition of manganese, but CDH degraded RDX anaerobically without addition of mediators. Attempts to improve biodegradation by supplementing cultures with micronutrients showed that addition of manganese and oxalate stimulated degradation rates in liquid, sawdust, and sand by the fungus, but not in loam soil. RDX degradation by P. chrysosporium in sawdust and sand was better than observed in liquid. However, degradation in solid matrices by the fungus only began after a lag period of 2 to 3 weeks, during which time extractable metabolites from wood were degraded.