1 2 Supplementary material Table S1: 3 Applied primer systems, DGGE gradient and acrylamide concentration (AA) (Ref. = Reference) Primer Target Gene [Function] Sequence 341f* 907r 803 16S rDNA Bacteria Me1f# Me2r Me3f* (500 bp) Methyl-coenzyme GCM ATG CAR ATH GGW ATG TC A reductase (mcrA) TCA TBG CRT AGT TDG GRT AGT [Methanogenesis] ATG TCN GGT GGH GTM GGS TTY AC CCT ACG GGA GGC AGC AG CCG TCA ATT CMT TTG AGT TT CTA CCA GGG TAT CTA ATC C Cycler Program Ref 95°C 5 min; 1 min 95°C, 1 [1–3] min 55°C, 1 min 72°C (35x); 10 min 72°C 95°C 5 min; 45 s 95°C, 45 s 50°C, 1.5 min 72°C (35 cycles); 10 min 72°C Gradi ent AA 40-65 7% [5, 6] 40-70 8% # 95°C 5 min; 45s 95°C, 45s 54°C, 45s 72°C (40x); 10 min 72°C nirS cd3af nirS3cdr** (500 bp) Cytochrome cd1depending nitrite reductase (nirS) [Denitrification] GTS AAC GTS AAG GAR ACS GG GAS TTC GGR TGS GTC TTG A 95°C 10 min; 45 s 95°C, 45s 60°C, 45 s 72°C (40x); 10 min 72°C [7] 40-70 8% nirK laCuf Copper-depending nirK3Cur** nitrite reductase (nirK) (450 bp) [Denitrification] ATC ATG GTS CTG CCG CG GCC TCG ATC AGR TTG TGG TT 95°C 10 min; 45 s 95°C, 45s 65°C, 45 s 72°C (40x); 10 min 72°C [7] 40-70 8% A189f# Particulate 682r methane mb661_nd monooxygenase (pmoA) [Methane oxidation] GGN GAC TGG GAC TTC TGG GAA SGC NGA GAA GAA SGC CCG GCG CAA CGT CCT TAC C 95°C 10 min; 45 s 95°C, 45s 61°C, 1min 72°C (35x); 10 min 72°C [12, 13] 35-65 7% 4 5 6 7 8 9 10 11 12 13 14 * GC clamp: CGC CCG CCG CGC CCC GCG CCC GTC CCG CCG CCC CCG CCC G **GC clamp: GGC GGC GCG CCG CCC GCC CCG CCC CCG TCG CCC G # semi-nested approach, first with Me1f and Me2r, second with Me2r and Me3f-gc, pmoA: first 189f and 682r, second 189f and mb661_nd 1 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 References: 1. Muyzer G, De Waal EC, Uitterlinden AG (1993) Profiling of complex microbial populations by denaturing gradient gel electrophoresis analysis of polymerase chain reaction-amplified genes coding for 16S rRNA. Appl Environ Microbiol 59:695–700. 2. Teske A, Sigalevich P, Cohen Y, Muyzer G (1996) Molecular identification of bacteria from a coculture by denaturing gradient gel electrophoresis of 16S ribosomal DNA fragments as a tool for isolation in pure cultures. Appl Environ Microbiol 62:4210–4215. 3. Lee SH, Malone C, Kemp PF (1993) Use of multiple 16S ribosomal RNA-targeted fluorescent probes to increase signal strength and measure celluar RNA from natural planktonic bacteria. Mar Ecol Prog Ser 101:193–201. doi: 10.3354/meps101193 4. Hales B, Edwards C, Ritchie D, et al. (1996) Isolation and identification of methanogen-specific DNA from blanket bog peat by PCR amplification and sequence analysis. Appl Env Microbiol 62:668–675. 5. Nunoura T, Oida H, Miyazaki J, et al. (2008) Quantification of mcrA by fluorescent PCR in methanogenic and methanotrophic microbial communities. FEMS Microbiol Ecol 64:240–247. 6. Throbäck IN, Enwall K, Jarvis A, Hallin S (2004) Reassessing PCR primers targeting nirS, nirK and nosZ genes for community surveys of denitrifying bacteria with DGGE. FEMS Microbiol Ecol 49:401–417. doi: 10.1016/j.femsec.2004.04.011 7. Holmes AJ, Costello A, Lidstrom ME, Murrell JC (1995) Evidence that participate methane monooxygenase and ammonia monooxygenase may be evolutionarily related. FEMS Microbiol Lett 132:203–208. 8. Holmes AJ, Costello A, Lidstrom ME, Murrell JC (1995) Evidence that participate methane monooxygenase and ammonia monooxygenase may be evolutionarily related. FEMS Microbiol Lett 132:203–208. 9. Lin J-L, Joye SB, Scholten JCM, et al. (2005) Analysis of methane monooxygenase genes in Mono Lake suggests that increased methane oxidation activity may correlate with a change in methanotroph community structure. Appl Environ Microbiol 71:6458–6462. 2