Journal
BIORESOURCE TECHNOLOGY
Volume 278, Issue -, Pages 180-186Publisher
ELSEVIER SCI LTD
DOI: 10.1016/j.biortech.2019.01.085
Keywords
Garden waste; Food waste; Co-fermentation; Caldicellulosiruptor saccharolyticus; Biochemical methane potential
Funding
- Portuguese Foundation for Science and Technology (FCT) [UID/BIO/04469/2013, POCI-01-0145-FEDER-006684, SAICTPAC/0040/2015, POCI-01-0145-FEDER-016403]
- BioTecNorte operation - European Regional Development Fund under the scope of Norte2020 - Programa Operacional Regional do Norte [NORTE-01-0145-FEDER-000004]
- FCT
- European Social Fund [SFRH/BPD/82000/2011]
- European Research Council under the European Union's Seventh Framework Programme (FP/2007-2013)/ERC Grant [323009]
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Co-fermentation of garden waste (GW) and food waste (FW) was assessed in a two-stage process coupling hyperthermophilic dark-fermentation and mesophilic anaerobic digestion (AD). In the first stage, biohydrogen production from individual substrates was tested at different volatile solids (VS) concentrations, using a pure culture of Caldicellulosiruptor saccharolyticus as inoculum. FW concentrations (in VS) above 2.9 g L-1 caused a lag phase of 5 days on biohydrogen production. No lag phase was observed for GW concentrations up to 25.6 g L-1. In the co-fermentation experiments, the highest hydrogen yield (46 +/- 1 L kg(-1)) was achieved for GW: FW 90: 10% (w/w). In the second stage, a biomethane yield of 682 +/- 14 L kg(-1) was obtained using the end-products of GW: FW 90: 10% co-fermentation. The energy generation predictable from co-fermentation and AD of GW: FW 90: 10% is 0.5 MJ kg(-1) and 24.4 MJ kg(-1), respectively, which represents an interesting alternative for valorisation of wastes produced locally in communities.
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