Microbial community development during syngas methanation in a trickle bed reactor with various nutrient sourcesShow others and affiliations
2022 (English)In: Applied Microbiology and Biotechnology, ISSN 0175-7598, E-ISSN 1432-0614, Vol. 106, p. 5317-5333Article in journal (Refereed) Published
Abstract [en]
Microbial community development within an anaerobic trickle bed reactor (TBR) during methanation of syngas (56% H2, 30% CO, 14% CO2) was investigated using three different nutrient media: defined nutrient medium (241 days), diluted digestate from a thermophilic co-digestion plant operating with food waste (200 days) and reject water from dewatered digested sewage sludge at a wastewater treatment plant (220 days). Different TBR operating periods showed slightly different performance that was not clearly linked to the nutrient medium, as all proved suitable for the methanation process. During operation, maximum syngas load was 5.33 L per L packed bed volume (pbv) & day and methane (CH4) production was 1.26 L CH4/Lpbv/d. Microbial community analysis with Illumina Miseq targeting 16S rDNA revealed high relative abundance (20–40%) of several potential syngas and acetate consumers within the genera Sporomusa, Spirochaetaceae, Rikenellaceae and Acetobacterium during the process. These were the dominant taxa except in a period with high flow rate of digestate from the food waste plant. The dominant methanogen in all periods was a member of the genus Methanobacterium, while Methanosarcina was also observed in the carrier community. As in reactor effluent, the dominant bacterial genus in the carrier was Sporomusa. These results show that syngas methanation in TBR can proceed well with different nutrient sources, including undefined medium of different origins. Moreover, the dominant syngas community remained the same over time even when non-sterilised digestates were used as nutrient medium. Key points: •Independent of nutrient source, syngas methanation above 1 L/Lpbv/D was achieved. •Methanobacterium and Sporomusa were dominant genera throughout the process. •Acetate conversion proceeded via both methanogenesis and syntrophic acetate oxidation. Graphical abstract: [Figure not available: see fulltext.] © 2022, The Author(s).
Place, publisher, year, edition, pages
Springer Science and Business Media Deutschland GmbH , 2022. Vol. 106, p. 5317-5333
Keywords [en]
Methanation, Methanobacterium, Microbial community, Sporomusa, Syngas, Trickling bed reactor, Anaerobic digestion, Biogas, Chemical reactors, Effluents, Hydrogenation, Nutrients, Sewage sludge, Sludge digestion, Synthesis gas, Wastewater treatment, Wetlands, Bed reactors, Digestate, Microbial communities, Nutrient media, Nutrient sources, Sporomusum, Syn gas, Tricklebed reactors, Packed beds
National Category
Microbiology
Identifiers
URN: urn:nbn:se:ri:diva-59865DOI: 10.1007/s00253-022-12035-5Scopus ID: 2-s2.0-85133622400OAI: oai:DiVA.org:ri-59865DiVA, id: diva2:1685112
Note
Funding details: Svenska Forskningsrådet Formas, 2018–01341; Funding details: Sveriges Lantbruksuniversitet, SLU; Funding details: Energimyndigheten, 45261–1; Funding text 1: Open access funding provided by Swedish University of Agricultural Sciences. This project was funded by the Swedish Energy Agency [45261–1] and Formas (2018–01341), and by participating partners, Cortus Energy, Sveaskog, Höganäs kommun, Gasum, Wärtsilä Biogas Systems, KTH, RISE and SLU, all acknowledged for their active contributions to the project.
2022-08-012022-08-012024-07-28Bibliographically approved