From: Direct interspecies electron transfer mechanisms of a biochar-amended anaerobic digestion: a review
Conductive materials | Substrate | Favorable change concerning control | References | ||
---|---|---|---|---|---|
CH4 yield (%) | Lag phase reduction (%) | COD removal (%) | |||
BC | Acetate | 22.6 | 1.5 | – | [142] |
Ethanol | 14.4 | 7.1 | – | [142] | |
Kitchen waste | 30 | – | 7 | [143] | |
Food waste | 33.2 |  | 60–88 | [144] | |
Simulated carbohydrate-rich food waste | 6.2 | 41 | – | [102] | |
Sewage sludge from WWTP | 55.9 | 61 | – | [4] | |
Glucose | – | – | 21.6 | [126] | |
Hydrochar | Artificial N-rich substrates | 32 | Â | 27.1 | [53] |
Pyrochar | Artificial N-rich substrates | – | – | 10.8–20.3 | [53] |
GAC | Kitchen waste | 26 | 29 | Â | [145] |
Dog food | Increased by 16-fold | – | 212 | [146] | |
Fat, oil and grease, and waste-activated sludge | 6.7–13.4 | 200–400 | 55.1–58.5 | [147] | |
PAC | Dry anaerobic digestion of sewage sludge | 49 | 16.6–58.3 | – | [148] |
Flammulina velutipes residues | – | 26.6 | – | [149] |