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Biological waste degradation is the main driving factor for landfill emissions. In a 2-year laboratory experiment simulating different landfill in-situ aeration scenarios, the microbial degradation of solid waste under different oxygen conditions (treatments) was investigated. Nine landfill simulation reactors were operated in triplicates under three distinct treatments. Three were kept anaerobic, three were aerated for 706 days after an initial anaerobic phase and three were aerated for 244 days in between two anaerobic phases. In total, 36 solid and 36 leachate samples were taken. Biolog® EcoPlates™ were used to assess the functional diversity of the microbial community. It was possible to directly relate the functional diversity to the biodegradability of MSW (municipal solid waste), measured as RI 4  (respiration index after 4 days). The differences between the treatments in RI 4  as well as in carbon and polymer degradation potential were small. Initially, a RI 4  of about 6.5 to 8 mg O 2  kg −1  DW was reduced to less than 1 mg O 2  kg −1  DW within 114 days of treatment. After the termination of aeration, an increase 3 mg O 2  kg −1  DW was observed. By calculating the integral of the Gompertz equation based on spline interpolation of the Biolog® EcoPlates™ results after 96 h two substrate groups mainly contributing to the biodegradability were identified: carbohydrates and polymers. The microbial activity of the respective microbial consortium could thus be related to the biodegradability with a multilinear regression model.

The microbial metabolic activity on carbohydrates and polymers impact the biodegradability of landfilled solid waste