|
Data
|
S
|
α
|
k
F
|
k
L
|
R
2
|
Sa
|
α
a
|
R
2a
|
---|
(mL g−1 VS)
|
(mL g− 1 VS)
|
(−)
|
(d− 1)
|
(d− 1)
|
(−)
|
(mL g− 1 VS)
|
(−)
|
(−)
|
---|
ESC1
|
206
|
260
|
0.70
|
0.1263
|
0.0120
|
1.00
|
220
|
0.19
|
1.00
|
ESC2
|
166
|
161
|
0.50
|
0.1508
|
0.1506
|
0.99
|
180
|
0.30
|
0.98
|
ESG1
|
228
|
231
|
0.46
|
0.1095
|
0.1094
|
1.00
|
252
|
0.12
|
0.99
|
ESG2
|
224
|
275
|
0.73
|
0.1707
|
0.0113
|
1.00
|
238
|
0.40
|
1.00
|
EN
|
219
|
218
|
0.59
|
1.0899
|
0.1315
|
1.00
|
213
|
0.97
|
0.94
|
- aOptimized values (curve fitting) for fixed parameter values of kF = 0.3393 (d−1) and kL = 0.0780 (d−1), respectively. Fixed first-order reaction constants were calculated as the mean value of the individual kinetic parameters (kF and kL) over all experiments
- Data final experimental value of the discontinuous digestion test (according to VDI 4630 [12]), S estimated total methane potential (at infinite retention time), α ratio of rapidly degradable substrate to total degradable substrate, k
F
first-order reaction constant for rapidly degradable substrate components, k
L
first-order reaction constant for slowly degradable substrate components, R2 coefficient of determination