Period I - Step feeding start-up Sample I II III V IV VI VII VIII Period II - Continuous Operation Sample III VI VII University of Minho School of Engineering.

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Period I - Step feeding start-up Sample I II III V IV VI VII VIII Period II - Continuous Operation Sample III VI VII University of Minho School of Engineering Centre of Biological Engineering Uma Escola a Reinventar o Futuro – Semana da Escola de Engenharia - 24 a 27 de Outubro de 2011 Introduction Even though some authors report LCFA as toxic towards microorganisms, in particular to methanogenic archaea, (Lalman & Bagley, 2001; Perle et al., 1995; Hwu & Lettinga, 1997) others considered the adverse effect of LCFA towards microbial communities reversible and mainly attributed to mass transfer limitations (Alves et al., 2001; Pereira et al., 2003; Pereira et al., 2004). The work developed by Cavaleiro et al. (2009) opened new perspectives on the anaerobic digestion of LCFA containing wastewaters when these authors demonstrated that continuous high rate treatment of oleic acid rich wastewater is possible if the appropriate conditions for biomass acclimatization to LCFA are applied. In this way, the energy stored in LCFA can be recovered coupling wastewater treatment to bioenergy production. In this work, the composition and dynamics of the archaeal community that colonized the anaerobic bioreactor from Cavaleiro et al. (2009) was investigated by using molecular tools. Methods Author* ANDREIA F. SALVADOR Supervisor: Diana Z. Sousa, Co-Supervisor: Madalena Alves * ENDURANCE OF METHANOGENIC ARCHAEA IN ANAEROBIC BIOREACTORS TREATING OLEATE BASED WASTEWATER After a step feeding start- up during 213 days the reactor was operated in continuous with organic loading rates from 5 to 31 kg COD m -3 day -1 (Cavaleiro et al., 2009) INOCULUM: Suspended biomass from a municipal anaerobic sludge digester Acclimated to fat Figure 1. Experimental set-up FEED: 50 % COD-sodium oleate 50 % COD-skim milk OPERATING CONDITIONS 37ºC Feed Effluent Recycle Biogas 37ºC Feed Effluent Recycle Biogas Total DNA isolation 16S rRNA gene amplification Microbial diversity and shifts PCRDGGE ARCHAEAL COMMUNITY DYNAMICS CloningSequencing Results Figure 2. DGGE pattern of archaeal 16S rDNA fragments and cluster analysis of DGGE profiles obtained from samples collected during Periods I and II. Numbers I to VIII indicate the bands that were identified by cloning and sequencing. Conclusions The identity of the most abundant methanogenic players during the start-up period (Period I) and the continuous operation (Period II) of a bioreactor treating LCFA-based wastewater was investigated. The 16S rRNA sequences identified are mostly related to those belonging to Methanosaeta and Methanobacterium genera. These archaea not only survived but were also able to maintain a high methanogenic activity during both operational periods. The results also suggest that these microorganisms are not as sensitive to the adverse effect of LCFA as they are often described. Moreover, these archaea could tolerate high LCFA concentrations in high rate bioreactors showing that in fact they are more resistant that previously thought. References Alves et al. (2001) Wat Res 35(1), Cavaleiro et al. (2009) Environ Sci Technol 43,2931–2936. Hwu C-S and Lettinga G (1997) Enzym Microb Technol 21, Lalman JA and Bagley DM (2001) Wat Res 35(12),2975–2983. Pereira et al. (2003) Water Sci Technol 48(6),33–40. Pereira et al. (2004) Biotechnol Bioeng 88(4), Perl et al. (1995) Wat Res 29(6), Acknowledgements: The financial support from Fundação para a Ciência e a Tecnologia (FCT) through the PhD grant SFRH/BD/48960/2008 given to Salvador AF is gratefully acknowledged. Methanobacteriales Methanosarcinales I EuryarchaeotaMethanobacterium beijingense % Euryarchaeota Methanobacterium sp. OM1599 %Euryarchaeota Methanosaeta concilii GP-699 %Euryarchaeota SEQUENCING RESULTS Band ID Closest Relative Identity Phylum Order II III V VI Figure 3. Sequences identity to those present in NCBI database according to NCBI-BLAST similarity searches. Methanobacterium beijingense 8-2 Methanobacteriales Methanobacterium sp. OM1599 %Euryarchaeota IV Methanobacteriales Methanosarcinales Methanosaeta concilii GP-699 %Euryarchaeota Methanosarcinales Methanosaeta concilii GP-699 %Euryarchaeota VII VIII Methanosarcinales Methanosaeta concilii GP-699 %Euryarchaeota