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Table 1 Reactor performances in thermophilic BER + CFT and previous reactors treating garbage waste under the maximum OLR conditions

From: Efficient production of methane from artificial garbage waste by a cylindrical bioelectrochemical reactor containing carbon fiber textiles

 

Treating waste

OLR (g-CODcr · L −1 · day −1)

HRT (days)

CODcr removal ratio (%)

VTS removal ratio (%)

SS removal ratio (%)

VSS removal ratio (%)

Gas production rate a(L · L −1 · day −1)

Methane content (%)

CODcr recovery b(%)

References

Cylindrical BER + CFT

10% AGS

89.3

1.5

62.5

-

52.5

50.9

16.5 ± 3.4

56.8

83.9

In this study

53.6

2.5

67.0 ± 3.5

-

56.6 ± 5.3

51.7 ± 4.9

12.1 ± 1.5

58.2 ± 1.7

117.1 ± 13.9

Packed-bed reactor

1.5% AGS + 1.0% milled paper

53.6

0.9

67.0

-

-

67.0

11.4

60.0

56.2

Ueno et al. (2007)

Small-scale BER + CFT (−0.8 V)

10% AGS + 0.08% ground rice straw

27.8

4.4

58.0 ± 4.9

-

38.9 ± 1.9

-

7.9 ± 0.7

55.0 ± 3.2

86.5 ± 2.6

Sasaki et al. (2011b)

CFSTR

10% artificial kitchen waste

20.4

11.0

89.0

 

-

-

-

-

82.0

Park et al. (2008)

UAF reactor

Synthetic garbage + swine manure

17.6

9.2

-

78.0

-

-

8.7

50.0

-

Liu et al. (2009)

CFSTR

2% AGS

6.25

4.0

65.8 ± 2.8

-

61.8 ± 5.6

-

1.8 ± 0.1

80.0

-

Sasaki et al. (2011c)

  1. aMean values under standard temperature and pressure at these OLRs are shown.
  2. bCODcr recovery = [(CODcr of the fermentation broth) + (CODcr of CH4)] / Influent CODcr.
  3. VTS: volatile total solid, SS: suspended solid, VSS: volatile suspended solid, UAF reactor: upflow anaerobic filter reactor, CFSTR: continuously flow-stirred tank reactor, AGS: artificial garbage slurry (dog food slurry).