Water 2016, 8, 172 S1 of S7 Supplementary Materials: Effects of Wash-Out Dynamics on Nitrifying Bacteria in Aerobic Granular Sludge During Start-Up at Gradually Decreased Settling Time Enikö Szabó, Malte Hermansson, Oskar Modin, Frank Persson and Britt-Marie Wilén Figure S1. Micrographs of the sludge in R1 (A) and R2 (B) taken 10 days after start-up. Water 2016, 8, 172; doi:10.3390/w8050172 www.mdpi.com/journal/water Water 2016, 8, 172 Figure S2. Micrographs of the sludge in R1 (A) and R2 (B) taken 28 days after start-up. S2 of S7 Water 2016, 8, 172 S3 of S7 Figure S3. Results of the qPCR analyses. Gene copy numbers of AOB amoA (a); and Universal 16S rRNA (b). Water 2016, 8, 172 Figure S4. Relative abundance of TRFs. Samples are marked with the identifier of the reactor (R1 or R2) and the number of days since start-up. SS = seed sludge. S4 of S7 Water 2016, 8, 172 S5 of S7 Figure S5. Effluent TSS concentration in the reactors. Figure S6. The impact of settling time on the SRT during start-up. The changes in settling time (min) are indicated with arrows and Arabic numerals. Figure S7. Variation of the pH in the reactors (measured at the end of the cycles). Water 2016, 8, 172 S6 of S7 Figure S8. Typical pattern of pH variation during a cycle in R1 (a) and R2 (b). The gray line marks the five minute anaerobic filling, i.e., the beginning of the cycle. Table S1. Primer pairs and annealing temperatures used for PCR and qPCR analysis. Primer Pairs amoA1F amoA2R CTO189A/B/C CTO654 FGPS872 FGPS1269 Nsr1113F Nsr1264R Uni1055F Uni1392R Target Organism AOB (Betaproteobacteria) AOB (Betaproteobacteria) Application Annealing Temp. (°C) Detection PCR and qPCR 54 + PCR and qPCR 57 + Degrange and Bardin 1995 Nitrobacter sp. PCR 50 – Dionisi et al. 2002 Nitrospira sp. PCR and qPCR 65 + Ferris et al. 1996 Most bacteria PCR and qPCR 54 + Reference Rotthauwe et al. 1997 Kowalchuk et al. 1997 References 1. 2. Degrange, V; Bardin, R. Detection and counting of Nitrobacter populations in soil by PCR. Appl. Environ. Microbiol. 1995, 61, 2093–2098. Dionisi, H.M.; Layton, A.C.; Harms, G.; Igrid, R.; Robinson, K.G.; Sayler, G.S. Quantification of Nitrosomonas oligotropha -Like Ammonia-Oxidizing Bacteria and Nitrospira spp. from Full-Scale Wastewater Treatment Plants by Competitive PCR. Appl. Environ. Microbiol. 2002, 68, 245–253. Water 2016, 8, 172 3. 4. 5. S7 of S7 Ferris, M.J.; Muyzer, G.; Ward, D.M. Denaturing gradient gel electrophoresis profiles of 16S rRNAdefined populations inhabiting a hot spring microbial mat community. Appl. Environ. Microbiol. 1996, 62, 340–346. Kowalchuk, G.A.; Stephen, J.R.; De Boer W, Prosser, J.I.; Embley, T.M.; Woldendorp, J.W. Analysis of ammonia-oxidizing bacteria of the beta subdivision of the class Proteobacteria in coastal sand dunes by denaturing gradient gel electrophoresis and sequencing of PCR-amplified 16S ribosomal DNA fragments. Appl. Environ. Microbiol. 1997, 63, 1489–1497. Rotthauwe, J.H.; Witzel, K.P.; Liesack, W. The ammonia monooxygenase structural gene amoA as a functional marker: molecular fine-scale analysis of natural ammonia-oxidizing populations. Appl. Environ. Microbiol. 1997, 63, 4704–471.
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