Landfilling represents the most economical method for the disposal of munic
ipal solid waste (MSW). After depletion of the limited volume of air availa
ble in void spaces of a waste bed, decomposition in a landfill takes place
under anaerobic conditions. Anaerobic digestion requires moisture and a lac
k of water is generally responsible for retarding degradation of MSW in con
ventional landfills. Furthermore, the moisture that may be present is seldo
m uniformly distributed. Bioreactor landfills are being researched as a mea
ns to provide a rapid and predictable stabilisation of waste and landfill g
as production. This is achieved primarily by control and management of the
liquid flow within the landfill.
The moisture content of waste and moisture movement through a waste bed are
two distinct factors that affect MSW decomposition. A moist environment is
critical for microbial activity; and flow of moisture is essential to mobi
lize nutrients and evenly distribute microorganisms through a waste bed. Th
e movement of moisture through a waste bed also provides improved mass tran
sfer and prevents the development of stagnant zones.
Experiments were carried out to understand how the amount of recirculated l
eachate effects waste degradation in coupled pairs of stabilised and fresh
waste reactors, Higher recirculation rates are shown to both improve solubi
lisation of fresh waste, and also establish the methanogenic microbial Copu
lation more quickly. In the best case, the organic fraction of the waste wa
s essentially entirely degraded within 2 months.