Biochar |
10 g/L |
75 μm |
Glucose |
Lag phase decreased by 38.0%. |
Shortening Lag Period and Start-Up Time |
Luo et al., 2015
|
Carbon nanotube |
1 g/L |
1–2 nm |
Glucose |
Start-up period shortened by around 40%. |
Shortening Lag Period and Start-Up Time |
Yan et al., 2017
|
Biochar |
15 g/L |
0.25–1 mm |
Phenol |
Lag phase decreased from 15.0 days to 1.1–3.2 days |
Shortening Lag Period and Start-Up Time |
Wang et al., 2020a
|
Hematite or magnetite |
25 mmol/L Fe |
– |
Benzoate |
Lag phase shortened by 8–12 days |
Shortening Lag Period and Start-Up Time |
Zhuang et al., 2015
|
Biochar |
2–15g/L |
0.25–1 mm |
Activated and food waste |
Lag time decreased by 27.5–64.4%. |
Shortening Lag Period and Start-Up Time |
Wang P. et al., 2018a
|
Fe3O4
|
10 g/L |
– |
Synthetic wastewater |
Lag time decreased by 13.9%. |
Shortening Lag Period and Start-Up Time |
Yin et al., 2017b
|
Biochar |
20 g/L |
– |
VFAs |
Lag phase shortened by 9.1–29.2%. |
Shortening Lag Period and Start-Up Time |
Wang et al., 2020b
|
GAC |
6 g/L |
<100 μm |
Acetic acid and ethanol |
CH4 yield increased by 31%. |
Improving Methane Yield |
Park et al., 2018b
|
GAC |
– |
8–20 mesh |
Lipid-rapeseed oil |
CH4 yield increased by 3.9 times. |
Improving Methane Yield |
Zhang et al., 2020
|
Biochar |
10 g/L |
10–15 mm |
Kitchen wastes and waste sludge |
CH4 yield increased by about 44%. |
Improving Methane Yield |
Li et al., 2020a
|
Biochar |
0.5–1.5 g/g⋅VS |
100 mesh |
Food waste and sewage sludge |
Lag time of CH4 production decreased. |
Improving Methane Yield |
Jiang et al., 2020
|
Activated carbon |
2–12 g/L |
180–200 mesh |
Sewage sludge |
CH4 yields improved by 124.0–146.3%. |
Improving Methane Yield |
Sun et al., 2020
|
Graphene |
30 and 120 mg/L |
Nano |
Glucose |
CH4 yields increased by 17.0 and 51.4%, respectively. |
Improving Methane Yield |
Tian et al., 2017
|
Carbon-based materials |
– |
– |
Dog food |
Higher organic loading rates were permitted. |
Enhancing System Stability |
Dang et al., 2016
|
Carbon-based materials |
– |
– |
Municipal solid waste |
CH4 production was promoted under high VFAs concentrations. |
Enhancing System Stability |
Dang et al., 2017
|
Biochar |
10 g/L |
2–5 mm |
Glucose |
Lag phase shortened and CH4 yields were improved. |
Enhancing System Stability |
Lu et al., 2016
|
Magnetite |
25 mmol/L Fe |
50–100 nm |
Pig manure |
CH4 yields increased with high ammonia concentrations. |
Enhancing System Stability |
Zhuang et al., 2018
|
Magnetite |
20 mmol/L Fe |
1.2 ± 0.2 μm |
Artificial wastewater |
CH4 production was increased 3–10 folds. |
Enhancing System Stability |
Jin et al., 2019
|
Stainless steel |
25.7 g/L |
0.5–2 mm |
Artificial wastewater |
CH4 production increased by 7.5–24.6%. |
Enhancing System Stability |
Li et al., 2017
|