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Table 1 Studied AD reactors and their physicochemical characteristics

From: A year of monitoring 20 mesophilic full-scale bioreactors reveals the existence of stable but different core microbiomes in bio-waste and wastewater anaerobic digestion systems

Reactor type

Main feeding substrate

AD unit

Reactor acronym

Reactor category

pH

Temp. range  °C

TIC

NH4–N

TS

VS

On-farm AD reactors fed mainly with agricultural residues

Maize and grass silages, cow manure and slurry (around 70%), bread

U-1

B

Fd

7.9 ± 0.2

39–40

3.4 ± 0.9

3.3 ± 0.9

8.6 ± 2.2

72.1 ± 4.8

Maize silage, cow manure (around 70%), minor food waste

U-2

C

Fd

8.0 ± 0.1

42–44

4.7 ± 0.6

3.9 ± 1.1

10.2 ± 1.4

72.6 ± 2.9

AD reactors treating a mixture of agricultural residues (mainly manure) and bio-waste

Cow manure and slurry, grass, maize and cereal silages, diary waste

U-3

BKA

Fd-1

7.6 ± 0.2

33–39

2.7 ± 0.4

2.1 ± 0.6

8.3 ± 0.6

72.9 ± 2.9

BKB

Fd-2

7.7 ± 0.2

2.9 ± 0.6

2.1 ± 0.6

8.0 ± 0.9

72.5 ± 2.9

BKC

Pd-1

7.9 ± 0.2

3.3 ± 0.3

2.6 ± 0.9

7.2 ± 0.3

69.5 ± 1.9

BKD

Pd-2

7.9 ± 0.2

3.3 ± 0.4

2.6 ± 0.7

7.3 ± 0.4

69.1 ± 1.8

BKE

St

7.8 ± 0.2

nh

3.6 ± 0.3

2.9 ± 0.5

6.7 ± 0.5

67.1 ± 1.9

Cow manure and slurry, cereal waste, waste from food industries, maize silage, grass

U-4

F-R1

Fd-1

7.8 ± 0.1

39

3.9 ± 0.5

3.5 ± 0.8

10.1 ± 0.8

65.9 ± 1.9

F-R2P

Pd

7.9 ± 0.1

5.6 ± 0.5

4.5 ± 0.8

8.5 ± 0.6

61.2 ± 1.2

F-R3

Fd-3

7.9 ± 0.1

4.8 ± 0.6

3.8 ± 0.8

8.8 ± 0.5

62.5 ± 1.6

F-stock

St

7.9 ± 0.1

nh

6.2 ± 0.5

5.0 ± 0.9

7.6 ± 0.4

57.6 ± 2.5

Manure, cereal waste, grass silage, organic waste from supermarkets and canteens

U-5

MbioA

Fd-1

7.5 ± 0.2

37–38

3.5 ± 0.7

3.6 ± 1.5

6.7 ± 0.9

66.5 ± 2.5

MbioB

Fd-2

7.6 ± 0.2

2.3 ± 0.4

1.9 ± 1.1

10.8 ± 3.7

70.6 ± 2.6

MbioC

Pd

7.6 ± 0.1

3.3 ± 0.5

2.7 ± 1.1

8.8 ± 0.9

68.1 ± 2.2

MbioD

St

7.6 ± 0.2

nh

3.5 ± 0.4

2.8 ± 0.6

7.7 ± 1.7

65.7 ± 2.4

Manure, green waste, maize silage, waste from food industries

U-6

NK

Fd

7.6 ± 0.3

36–37

3.4 ± 0.6

2.4 ± 0.8

7.8 ± 0.9

66.2 ± 2.2

Municipal and green waste treating AD reactors

Yard green waste (leaves, trees), organic waste from households and canteens

U-7

MK-beg

Fd

7.8 ± 0.2

39

4.9 ± 0.8

3.6 ± 1.5

21.6 ± 1.6

50.8 ± 2.7

MK-mid

7.8 ± 0.2

4.6 ± 0.8

3.4 ± 1.5

22.2 ± 1.3

51.7 ± 3.2

MK-end

7.8 ± 0.1

4.6 ± 0.9

3.5 ± 1.6

21.8 ± 1.7

50.7 ± 2.8

WWTP-specific AD reactors

Thickened sewage sludge from wastewater treatment

U-8

P

Fd

7.2 ± 0.1

35

1.3 ± 0.3

0.4 ± 0.5

2.5 ± 0.4

47.7 ± 3.3

U-9

S

Fd

7.1 ± 0.1

36

1.2 ± 0.2

0.7 ± 0.5

3.8 ± 0.4

55.6 ± 1.8

U-10

BT

Fd

7.2 ± 0.1

36

1.4 ± 0.2

1.3 ± 0.9

3.0 ± 0.2

49.0 ± 1.6

  1. Fd fed digester, Pd post-digester, St storage tank, TIC total inorganic carbon (m3 of CO2/m3 of sludge), NH4–N total ammonium–nitrogen (kg NH4–N/m3 of sludge), TS total solids (% of total solid/fresh sludge [w/w]), VS volatile solids (% of volatile solid/ % of total solid [w/w], nh non-heated