Table 68 Ranking of end-of-life options within each scenario for food and garden waste
Case Composting
Incineration
with energy
recovery
Landfill
Anaerobic
digestion
1[OR] +++ +
2[GW1] + +++
2[GW2] + +++
3[FW1] +++ +
3[FW2] +++ +
3[FW3]* + * +++
4[FW1] ++ ++ + +++
4[FW2] ++ ++ + +++
5[OR] +++ +++ +
6[OR] ++ ++ + +++
7[OR] +++ +
4[FW1] + ++ ++ +++
4[FW2] + ++ ++ +++
1[OR] ++++
3[FW1] ++++
3[FW2] +++ +
3[FW3]* +++ * +
4[FW1] + +++ ++ ++
4[FW2] + +++ ++ ++
5[OR] + +++ ++
3[FW1] +++ +
3[FW2] +++ +
3[FW3]* +++ * +
Only study n°3 includes this indicator
Water
consumption
(m^3 )
- (^) Composting scenario assuming total anaerobic degradation
Climate change
(kg CO 2 eq)
Only study n°4 includes this indicator
Depletion of
natural
resources
(kg Sb eq)
Studies n°2, 6 and 7 do not include this indicator
Energy demand
(MJ)
+++ best option
++ intermediary option
- worst option
option not assessed
3.5.3 Detailed comparison between the various treatment options
Climate change
The diagrams below indicate the relative difference of composting or incineration with energy recovery and the
rest of the treatment options.
One point regarding anaerobic digestion should be explained. The configuration of anaerobic digestion in all three
studies that include it shows quite high methane recovery efficiencies (methane capture is above 90-95%) and
conversion to energy. These numbers reveal the assumption that the anaerobic digestion plant is state-of-the-art,
which influences the results greatly and renders the comparisons to other treatment plants relatively unfair.
Moreover, it should be noted that study no 3 contains two cases of home composting. The first case assumes
fully aerobic conditions (case 3[FW2]), while the second assumes fully anaerobic conditions (case 3[FW3]). These