1 Supporting Information 2 3 Introduction 4 5 There are three primer sets frequently employed for AOA amoA quantification: Arch-amoAF 6 and Arch-amoAR (called the FranAOA primer set), were designed in 2005 using a limited set of 7 archaeal sequences and not originally intended for application in qPCR. The second set, 8 amo196F and amo277R, was designed by Treusch and others also in 2005 using archaeal amoA 9 sequences from soils (called the TreuAOA primer set). The third primer set, CrenAmoAQ-F and 10 CrenAmoAModR, published by Mincer and colleagues in 2007 was based on marine archaeal 11 sequences (called the MincAOA primer set). While the two later sets were designed specifically 12 for use in qPCR and produce small amplicons, they include numerous degenerate positions. 13 14 The most commonly used primer set to quantify AOB is amoA-1F and amoA-2R, developed by 15 Rotthauwe and others in 1997 (called the RottAOB primer set). These primers were not 16 specifically designed for qPCR, and the reverse primer contains two central degenerate positions. 17 18 Results 19 20 Specificity of newly designed archaeal and bacterial amoA primer sets. The specificity of 21 both new qPCR primer sets was confirmed via in silico and molecular analysis. A BLASTN 22 search of the NCBI website (NCBI) against the GenAOAF primer returned matches of 96-100% 23 identity (E value 9.0E-5) only to the ammonia monooxygenase (amoA) gene of thaumarchaeotes 1 24 and crenarchaeotes. The GenAOAR primer matched with 96-100% identity (E value 0.021) to 25 only the amoA of archaea and thaumarchaeotes. The amoA-1Fmod primer (for AOB) matched 26 with 100% identity (E value 0.028) only to the amoA of uncultured bacteria or to ammonia- 27 oxidizing beta proteobacteria, and the GenAOBF primer matched with 100% identity (E value 28 0.11) only to the amoA of uncultured bacteria. All amplicons were verified for correct size on 29 agarose gels and by sequencing of cloned amplification products. 30 31 Reaction parameters and statistics. A plasmid containing the 660 bp AOA amoA gene 32 fragment with fewest mismatches to all primer sets was used as the standard for AOA amoA 33 quantification. The standard curve produced a linear response over five orders of magnitude (R2 34 = 0.993 to 0.999, range for all reactions with all primer sets) with a detection limit of 10-100 35 copies per reaction. Loss of linearity below this was likely due to the formation of primer dimers 36 with some primer sets (often TreuAOA, occasionally MincAOA). For consistency, 100 copies 37 per reaction was selected as the lowest concentration in the standard series. The average 38 efficiency of all AOA quantification reactions with the FranAOA, TreuAOA, MincAOA, and 39 GenAOA primer sets was 84%, 99%, 86, and 95%, respectively. The lowest efficiency observed 40 (76%) was with the MincAOA primer set when quantifying the plasmid mixes, and the highest 41 observed (107%) was with the TreuAOA primer set when quantifying the single plasmids. 42 43 An equimolar mixture of two plasmids, each containing the 673 bp AOB amoA amplicon from 44 Nitrosomonas europaea and Nitrosospira briensis, was used as a standard and to determine the 45 reaction efficiency of the bacterial amoA primer sets. These two plasmids were mixed in order 46 to introduce a reasonable amount of sequence diversity within the standard (Nm europaea has 2 47 five mismatches between the two priming sites versus one mismatch in each of the Nsp briensis 48 priming sites). This plasmid mixture resulted in a linear amplification response (R2 = 0.994- 49 0.999 range for all reactions), with both the RottAOB and GenAOB primer sets having a 50 detection limit of 100 copies per reaction. Average reaction efficiencies were 90% for the 51 RottAOB and 97% for the GenAOB primer set. Efficiencies as low as 77% have been reported 52 when quantifying AOB in soils (Schauss et al., 2009), but values commonly range from 80% to 53 slightly over 100% (Nicol et al., 2008; Di et al., 2009; Jia and Conrad, 2009; Schauss et al., 54 2009). 55 56 Assessment of archaeal amoA amplification specificity via melt curve and gel analysis. The 57 specificity of each primer set in all qPCR assays was first assessed by observing product melt 58 curves. For the single plasmids, the product melt curves for the MincAOA, TreuAOA, and 59 GenAOA primer sets were narrow and unimodal. However, those for the FranAOA primer set 60 were bi-modal. For the mixed plasmid products, the melt curves for the MincAOA and 61 GenAOA primer sets were narrow and unimodal, but the TreuAOA products were bimodal and 62 multimodal for the FranAOA products. Melt curves from soil DNA samples were unimodal only 63 when the MincAOA primer set was used and for all samples but one (OM3) when the GenAOA 64 primer set was used. Conversely, the product melt curves from the TreuAOA and FranAOA 65 primer sets were multimodal for all samples and often had low amplitude. Melt curves for 66 standards were always sharp and unimodal, suggesting no problems with the standards or 67 reaction conditions. 68 3 69 The specificity of each primer set was next evaluated by visualization of the qPCR products on 70 an agarose gel (Fig. S4). This was conducted to reveal any potential misinterpretations of primer 71 specificity based solely on melt curves. In general, each primer set preferentially amplified one 72 product of expected size, however, depending on the primer set and the samples being analyzed 73 (plasmids or soil DNA), non-target amplification did occur, as was suggested by earlier 74 observation of the product melt curves. When amplifying AOA amoA genes from plasmids 75 (single or mixed), the FranAOA primer set consistently co-amplified a ~1 kb product. With soil 76 DNA samples, the FranAOA primer set produced an intense target band but also amplified many 77 small (< 500 bp) non-target fragments, especially from the OM samples. Visualization of the 78 TreuAOA primer set amplicons from plasmids showed single, discrete bands for all samples, 79 with some primer dimer present in the non-template control (NTC) and lower standard reactions. 80 With the soil DNA samples, a single product amplified by the TreuAOA primer set was observed 81 for samples PR1-3 and PAT1-2, but little to no target product was apparent in OM samples. 82 Instead, larger non-target fragments were observed. The MincAOA primer set chiefly amplified 83 the target fragment from plasmids, but three other, non-target bands were occasionally present. 84 With the soil DNA samples, the MincAOA primer set amplified many non-target fragments, 85 occasionally more efficiently than the target. Strangely, this observation was inconsistent with 86 the results of the melt curve analysis, which provided little indication of non-target amplification. 87 Lastly, the GenAOA primer set produced a single product from both single and mixed plasmid 88 templates and most soil DNA samples. Product bands appeared thicker for a few soil DNA 89 samples, suggesting similar migration of nearly identical-sized amplicons. 90 4 91 Assessment of bacterial amoA amplification specificity via melt curve and gel analysis. The 92 AOB amoA plasmid and soil DNA qPCR products were evaluated for specificity by melt curve 93 analysis. With the plasmid mixes, the product melt curves from the RottAOB primer set were 94 bimodal for the mixed samples and unimodal for the samples containing 100% of either Nsp 95 briensis or Nm europaea plasmid. The melt curves of the standards, containing a 50:50 mixture 96 of the two plasmids, were also bimodal. Primer dimer was detected in the NTC for the RottAOB 97 primer set. The product melt curves from the GenAOB primer set were unimodal for all 98 plasmids, and no primer dimer was detected in the NTC. The melt curves from one soil DNA 99 sample indicated the presence of non-target amplification with the RottAOB primer set. The 100 product melt curves for the GenAOB primer were unimodal, indicating no non-target 101 amplification. Again, primer dimer was detected with the RottAOB primer set in the NTC but 102 not with the GenAOB primer set. 103 104 Gel visualization of the qPCR products from the plasmids and soil DNA samples confirmed the 105 characteristics suggested by the melt curves for the AOB amoA amplicons. The plasmid qPCR 106 products from the RottAOB primer set showed a dominance of the target amplicon, but a ~1 kb 107 amplicon was co-amplified (Fig. S5). The TOPO sequence was verified to contain no target for 108 the RottAOB primer sequences, so this non-target amplification is definitely unexpected. This 109 larger product was not apparent in the melt curve analysis. The GenAOB primer set produced a 110 single, correct-sized product for all plasmid samples. Imaging of the RottAOB qPCR product 111 from the soil DNA samples verified the presence of non-target amplicons in one sample, OM3 112 (Fig. S6). A single amplicon was observed in all soil DNA sample products amplified using the 113 GenAOB primer set. 5 114 115 Experimental procedures 116 117 Soil DNA extraction, amoA amplification, clone library construction, and sequencing. 118 Primer design was based on published amoA sequences and sequences recovered from eight 119 surface (0-15 cm) soil samples collected from five sites in Washington, USA, each with differing 120 physical and chemical properties (Table 1). After evaluating three DNA extraction methods by 121 comparing total DNA yield, extent of DNA shearing, and amplification inhibition over a range of 122 dilutions (data not shown), DNA was extracted from 0.3 g homogenized soil using the MO BIO 123 PowerSoil DNA Isolation Kit (MO BIO Laboratories, Inc., Carlsbad, CA) with the bead-beating 124 step being completed in a FastPrep-24 Instrument (MP Biomedicals, Irvine, CA). The bead 125 beating speed and time (5.5 m/s for 30 s) was optimized by assessing total DNA yield and the 126 extent of DNA shearing. Soil DNA was diluted below the concentration required for qPCR, and 127 no inhibition was detected in end-point PCR (data not shown). Two extractions were performed 128 simultaneously and pooled. 129 130 End-point PCR was carried out in 20 µL reactions with final concentrations of 1X GoTaq Green 131 Master Mix (Promega Inc., Madison, WI), 0.4 ng/µL Bovine Serum Albumin, 0.25 µM of each 132 primer, and 10-20 ng sample DNA. Reactions were run in a BioRad C1000 thermal cycler 133 (BioRad, Hercules, CA). The FranAOA primer set and published thermoprofile (Francis et al., 134 2005) provided the longest amplicon of all the available primers sets and were used to amplify 135 the AOA amoA in each sample. The RottAOB primer set and published thermoprofile 136 (Rotthauwe et al., 1997) were used to amplify the AOB amoA in each sample. Resulting 6 137 amplicons (635 and 491 bp, respectively) were verified via agarose gel electrophoresis. The 138 PCR product was cleaned using the QIAquick PCR Purification kit (Qiagen, Valencia, CA), 139 cloned using the TOPO TA Cloning Kit with the pCR4-TOPO TA vector (Life Technologies, 140 Carlsbad, CA), and transformed into One Shot TOP10 Chemically Competent E. coli cells (Life 141 Technologies, Carlsbad, CA). After blue-white screening, 96 positive clones were picked into 142 100 µL of selective LB broth with 10% glycerol (final conc.) in culture plates. Plasmid 143 isolations and Sanger sequencing from the M13F priming site were performed on an ABI 3730xl 144 DNA Analyzer (ABI Life Sciences, San Diego, CA) by HTSeq, Inc. (Seattle, WA). 145 146 Design of archaeal amoA forward and bacterial amoA reverse primers. A total of 938 and 147 724 amoA clone library sequences for AOA and AOB, respectively, were used for internal 148 primer design. Three to five representative sequences from each major clade in the ARB 149 database were also selected for AOA primer design. The sequence variation in Nitrosopumilus 150 maritimus SCM1 and three new marine isolates was also considered. Separate alignments of 151 AOA and AOB amoA sequences were generated using the ClustalW Alignment option in the 152 Geneious 6.1.5 software package (Biomatters Ltd.) and by manual inspection. A conserved 153 region 85 nucleotides interior to the Arch-amoAR priming site, and in the same region targeted 154 by the Mincer CrenAmoAQ-F primer (Fig. 1), was selected for the design of a new archaeal 155 amoA forward qPCR primer, GenAOAF (see Table 2 for all primer sequences). Likewise for 156 AOB, GenAOBR was designed in a conserved region 80 nucleotides interior to the beginning of 157 the amoA-1F forward priming site (Fig. 1). 158 7 159 Selective recovery of environmental archaeal amoA sequences spanning the Arch-amoAR 160 primer binding site. Environmental archaeal amoA sequences within and flanking the Arch- 161 amoAR (FranAOA) target region were selectively recovered from soil DNA metagenomic 162 sequence libraries (Bertagnolli et al., in review; Table 1). Briefly, approximately 16 Gbp of 163 metagenomic data were generated from the eight soil DNA samples using the Illumina HiSeq 164 2000 platform. amoA reads were identified in cleaned metagenomic sequence data through 165 alignment (BLASTN, BLAST+ version 2.28) against AOA and AOB databases (Altschul et al., 166 1990). The primer AOAextR was designed after retrieval and alignment of over 190 167 metagenomic reads mapping near the Arch-amoAR priming site. 168 169 A clone library was constructed using the Arch-amoAF and AOAextR primers to amplify a 660 170 bp amoA fragment from selected soil DNA samples, as described above (50 °C annealing 171 temperature). In consideration of 85 resulting clone sequences presenting natural variation 172 within the Arch-amoAR target region in these field sites, and preliminary testing with several 173 primer variants (data not shown), we designed a new primer, GenAOAR (Table 2), by modifying 174 Arch-amoAR and extending its binding region (Figure 1). 175 176 Comparative amplification of divergent archaeal amoA sequences using single and mixed 177 plasmid templates. Two experiments were conducted using a collection of cloned amoA 178 sequence variants to evaluate the specificity and relative stoichiometry of amplification using the 179 newly designed GenAOAF and GenAOAR primers (hereafter called the GenAOA primer set) 180 and the other commonly used primer sets. A study set of 11 clones of the 660 bp amplicons 181 representative of environmental sequence variation within the GenAOAF and GenAOAR 8 182 priming sites were used for comparative analyses. In the first experiment, the AOA amoA gene 183 count obtained from the amplification of individual plasmids using the FranAOA, TreuAOA, 184 MincAOA, and GenAOA primer set was compared to the count determined using TOPO vector- 185 specific primer set. A TOPO primer set (TOPO4-2259F and TOPO4-2448R; Table 2) was 186 designed to provide an objective gene copy number unaffected by insert sequence diversity. 187 Plasmids were diluted to a concentration of 0.25 ng/µL, and a total of 1 ng (4 µL) of plasmid 188 DNA was added to a 6 µL reaction mixture containing 1X LightCycler FastStart DNA Master 189 SYBR Green I (Roche, Indianapolis, IN), 4.5 mM MgCl2 (optimized), and 0.5 µM of each 190 primer (final concentrations) in LightCycler glass capillaries. Reactions were performed in a 191 Roche LightCycler Carousel-Based System with software v3.5. The qPCR thermoprofile for the 192 GenAOA primer set was 95 C for 5 min; 45 cycles of 95 C for 10 s, 55 C (optimized by 193 gradient end-point PCR with multiple environmental samples and plasmids) for 10 s, 72 C for 194 13 s, followed by a single 3 s data collection at 84 C, increased to avoid detection of possible 195 primer-dimer fluorescence. Melt curves (65 °C held for 15 s with continuous measurement to 196 95°C), as well as product electrophoresis on an agarose gel, confirmed product specificity. 197 Thermoprofiles for the TreuAOA and MincAOA primer sets were as published (Treusch et al., 198 2005; Mincer et al., 2007), respectively, and the thermoprofile for the FranAOA primer set 199 followed that published by Di and colleagues (Di et al., 2009). Optimization of these 200 thermoprofiles was attempted after initial reaction efficiencies were lower than reported by the 201 respective authors, but for the soils tested in this study, conditions could not be improved. For 202 all primer sets, the initial 95 °C enzyme activation time was adjusted to 5 minutes, optimized for 203 the Taq used in these experiments. 204 9 205 The second qPCR comparison experiment evaluated the relative efficiencies of each archaeal 206 amoA primer set to amplify four simplified model communities, comprised of a mixture of two 207 or more plasmids. Composition of mixtures was determined by natural sequence diversity and 208 the results of an initial examination of amplification efficiency. One mixture included two 209 plasmids in which the relative concentration of the most poorly amplifying sequence type was 210 present in a ratio of either 80:20 or 20:80 with a sequence type amplifying with good efficiency. 211 A second mixture consisted of equimolar amounts of plasmids representing four of the five 212 dominant soil clades (Nitrososphaera 54d9, Nitrososphaera subclade 1.1, unclassified 213 Nitrososphaera clade 1 (non-54d9), and Nitrosotalea subclade 1.1; Bertagnolli et al., in review) 214 observed in our sampling sites. A final mixture consisted of all 11 plasmids mixed at equimolar 215 ratios. Reactions were carried out in duplicate as described above. 216 217 Comparative archaeal amoA primer amplification of soil DNA samples. Each primer set 218 was also used to quantify the total AOA amoA gene abundance in environmental soil samples. 219 DNA from eight soil samples (Table 1) was amplified with each of the four primer sets, as 220 detailed above, to survey the overall gene count variation, error, and non-target amplification 221 among them. Melt curve analysis was conducted, and products were analyzed on agarose gels to 222 check for non-target amplification. 223 224 To reduce variability associated with enzyme age or reagent stocks (Smith et al., 2006), each 225 comparative analysis was conducted in one to two days with a single aliquot of MgCl2, each 226 primer, and enzyme and SYBR Green mixture. A plasmid containing the 660 bp AOA amoA 227 amplicon with the fewest mismatches in each priming site served as the internal standard (106- 10 228 102 copies, duplicate reaction for 102 copies). Accuracy was improved by including a standard 229 in every assay, as opposed to applying a single standard to multiple assays. Although the use of 230 external standards is often reported (Treusch et al., 2005; Park et al., 2008; Di et al., 2009), a 231 single standard does not account for inter-assay variation caused by the experimenter, 232 preparation, reagents, or the reaction itself (Smith et al., 2006). This plasmid returned the best 233 overall efficiency for all reactions with all primer sets in preliminary qPCR tests (data not 234 shown). All samples were run in duplicate. 235 236 Redesign of the bacterial amoA forward primer. We aimed to pair amoA-1F either 237 unchanged or a similar sequence, in which no degeneracies would be included, with GenAOBR 238 to capture the greatest sequence diversity present within an AOB community. The design of a 239 new primer flanking the amoA-1F primer hybridization site was based on natural sequence 240 variation within this priming site found in soil metagenomic sequences. Since the number of 241 suitable metagenomic sequences was low (11 in total), publically-available, complete bacterial 242 amoA sequences from Nitrosospira multiformis, Nsp briensis, Nitrosomonas europaea, Nm 243 eutropha, Nm sp. Is79A3, and Nm sp. AL212 (accession numbers NC007614.1, U76553.1, 244 NC_004757.1, NC_008344.1, NC_015731.1, NC_015222.1, respectively), were also included 245 for the design. The alignment was used to design a new forward primer (AOBextF, Table 2) 246 beginning 161 nucleotides upstream of the amoA-1F priming site (Fig. 1). This primer is similar 247 to (3 nucleotide differences), and hybridizes to the same region as, the A189F primer developed 248 by Holmes and colleagues (Holmes et al., 1995). The amoA-2R and newly designed AOBextF 249 primers were then used (as described above, 58° C annealing temperature) to amplify a 673 bp 250 fragment from two cultured AOB species, Nm europaea and Nsp briensis. On the basis of initial 11 251 amplification results (data not shown), amoA-1F was modified by three nucleotides to create 252 amoA-1Fmod (Table 2). 253 254 Comparative bacterial amoA amplification using plasmids and soil DNA samples. The two 255 plasmids containing the 673 bp amplicons of AOB amoA gene sequences from Nm europaea and 256 Nsp briensis, and a set of soil DNA samples, were used to compare the RottAOB primer set with 257 that of amoA-1Fmod and GenAOBR (hereafter called the GenAOB primer set). The two 258 plasmids were quantified separately and in mixtures (80:20 Nm europaea: Nsp briensis and vice 259 versa) with the RottAOB, GenAOB, and TOPO primer set, following the reaction preparation 260 methods described above for the AOA primer sets. Additionally, bacterial amoA genes were 261 quantified in the same eight soil DNA samples used to evaluate the archaeal amoA primer sets. 262 The thermoprofile used with the GenAOB primer set was identical to that used for the GenAOA 263 primer set but with annealing at 58 °C. The qPCR thermoprofile for the RottAOB primer set 264 followed the protocol of Di and colleagues (Di et al., 2009), with an initial Taq activation of 5 265 min at 95 °C. The plasmids were quantified with the TOPO primer set, as described above. 266 Samples were run in duplicate and the internal standard was prepared as above but using a 50:50 267 mixture of the Nm europaea and Nsp briensis 673 bp amoA amplicon insert plasmids. 268 269 Utility of newly designed archaeal and bacterial amoA primer sets for isolates and diverse 270 environments. The efficacy of the new primer sets to amplify archaeal and bacterial amoA 271 sequences from different environments was tested by end-point and quantitative PCR. DNA 272 from three marine archaeal isolates (Qin et al., in press) was used to assess the specificity of the 273 new archaeal primer set to marine AOA in end-point PCR, following the methods described 12 274 above. Additionally, DNA from alpine soils was used to verify amplification and specificity of 275 both new primer sets in another environment using the aforementioned qPCR methods. 276 277 Comparison of metagenomic data with communities captured by new and conventional 278 primer sets. Clone libraries were constructed using the newly designed archaeal and bacterial 279 primer sets for one of the DNA samples (PAT1; Table 1) for which metagenomic and amplicon 280 clone sequence data (FranAOA and RottAOB primer set amplification) was available 281 (Bertagnolli et al., in review; Table 1). The resulting data allowed for comparison of the 282 community captured by each primer set relative to the less-biased metagenomic community 283 composition assessment. 284 285 Statistical analyses. The data from qPCR assays of the plasmids and plasmid mixtures are 286 presented as copies per ng of plasmid DNA. Raw data from qPCR assays of soil DNA samples 287 were converted to cells per g soil. For AOB, cells numbers were estimated by dividing gene 288 counts by 2.6, accounting for 2 copies of the amoA gene in each genome and 1.3 genomes per 289 cell (Hermansson and Lindgren, 2001). When normally distributed, data were analyzed by one- 290 or two-way (when testing for an interaction) analysis of variance (ANOVA), followed by Tukey- 291 Kramer post hoc HSD comparisons to pinpoint significant differences among primer sets. The 292 AOA and AOB amoA soil DNA gene count data were log-transformed to normality. If the data 293 could not be successfully transformed to normality, the nonparametric Kruskal-Wallis test was 294 used. These analyses were performed in the statistical software package SPSS 19.0 with a 295 significance cut-off of P ≤ 0.05. Taxonomic assignment of AOA and AOB were based on the 13 296 work of Pester and others (2012) and Avrahami and Conrad (2003), respectively (Bertagnolli et 297 al., in review). 298 299 References 300 301 Altschul, S.F., Gish, W., Miller, W., Myers, E.W., and Lipman, D.J. (1990) Basic Local 302 Alignment Search Tool. Journal of Molecular Biology 215: 403-410. 303 Di, H.J., Cameron, K.C., Shen, J.P., Winefield, C.S., O/'Callaghan, M., Bowatte, S., and He, J.Z. 304 (2009) Nitrification Driven by Bacteria and Not Archaea in Nitrogen-Rich Grassland Soils. 305 Nature Geoscience 2: 621-624. 306 Francis, C.A., Roberts, K.J., Beman, J.M., Santoro, A.E., and Oakley, B.B. (2005) Ubiquity and 307 Diversity of Ammonia-Oxidizing Archaea in Water Columns and Sediments of the Ocean. 308 Proceedings of the National Academy of Sciences of the United States of America 102: 14683- 309 14688. 310 Hermansson, A., and Lindgren, P.-E. (2001) Quantification of Ammonia-Oxidizing Bacteria in 311 Arable Soil by Real-Time Pcr. Applied and Environmental Microbiology 67: 972-976. 312 Holmes, A.J., Costello, A., Lidstrom, M.E., and Murrell, J.C. (1995) Evidence That Particulate 313 Methane Monooxygenase and Ammonia Monooxygenase May Be Evolutionarily Related. FEMS 314 Microbiology Letters 132: 203-208. 315 Jia, Z., and Conrad, R. (2009) Bacteria Rather Than Archaea Dominate Microbial Ammonia 316 Oxidation in an Agricultural Soil. Environmental Microbiology 11: 1658-1671. 14 317 Mincer, T.J., Church, M.J., Taylor, L.T., Preston, C., Karl, D.M., and DeLong, E.F. (2007) 318 Quantitative Distribution of Presumptive Archaeal and Bacterial Nitrifiers in Monterey Bay and 319 the North Pacific Subtropical Gyre. Environmental Microbiology 9: 1162-1175. 320 NCBI Basic Local Alignment Tool (Blast). URL http://blast.ncbi.nlm.nih.gov/Blast.cgi 321 Nicol, G.W., Leininger, S., Schleper, C., and Prosser, J.I. (2008) The Influence of Soil Ph on the 322 Diversity, Abundance and Transcriptional Activity of Ammonia Oxidizing Archaea and 323 Bacteria. Environmental Microbiology 10: 2966-2978. 324 Park, S.-J., Park, B.-J., and Rhee, S.-K. (2008) Comparative Analysis of Archaeal 16s Rrna and 325 Amoa Genes to Estimate the Abundance and Diversity of Ammonia-Oxidizing Archaea in 326 Marine Sediments. Extremophiles 12: 605-615. 327 Rotthauwe, J.H., Witzel, K.P., and Liesack, W. (1997) The Ammonia Monooxygenase Structural 328 Gene Amoa as a Functional Marker: Molecular Fine-Scale Analysis of Natural Ammonia- 329 Oxidizing Populations. Applied and Environmental Microbiology 63: 4704-4712. 330 Schauss, K., Focks, A., Leininger, S., Kotzerke, A., Heuer, H., Thiele-Bruhn, S. et al. (2009) 331 Dynamics and Functional Relevance of Ammonia-Oxidizing Archaea in Two Agricultural Soils. 332 Environmental Microbiology 11: 446-456. 333 Smith, C.J., Nedwell, D.B., Dong, L.F., and Osborn, A.M. (2006) Evaluation of Quantitative 334 Polymerase Chain Reaction-Based Approaches for Determining Gene Copy and Gene Transcript 335 Numbers in Environmental Samples. Environmental Microbiology 8: 804-815. 15 336 Treusch, A.H., Leininger, S., Kletzin, A., Schuster, S.C., Klenk, H.-P., and Schleper, C. (2005) 337 Novel Genes for Nitrite Reductase and Amo-Related Proteins Indicate a Role of Uncultivated 338 Mesophilic Crenarchaeota in Nitrogen Cycling. Environmental Microbiology 7: 1985-1995. 339 340 341 342 343 344 345 346 347 348 349 350 351 352 353 354 355 356 357 358 16 359 360 Table S1. qPCR reaction statistics for AOA primer sets and experimental comparisons. Primer set Comparison Slope Efficiency (%) Intercept R2 FranAOA Single plasmids Plasmid mixes Soil DNA samples -3.63 -3.86 -3.80 88.5 81.5 83.3 39.48 39.51 38.70 -0.999 -0.998 -0.999 TreuAOA Single plasmids Plasmid mixes Soil DNA samples -3.17 -3.46 -3.41 107.0 94.7 96.3 39.48 39.54 39.40 -0.996 -0.995 -0.999 MincAOA Single plasmids Plasmid mixes Soil DNA samples -3.67 -4.07 -3.49 87.3 76.0 93.5 42.59 44.42 41.15 -0.993 -0.997 -0.995 GenAOA Single plasmids Plasmid mixes Soil DNA samples -3.55 -3.45 -3.34 91.2 94.9 99.3 40.03 39.44 38.72 -0.999 -0.999 -0.999 361 362 363 364 365 366 367 368 369 370 371 372 373 374 17 375 376 Table S2. qPCR reaction statistics for AOB primer sets and experimental comparisons. Comparison Slope Efficiency (%) RottAOB Plasmid mixes Soil DNA samples -3.56 -3.61 91.0 89.3 38.27 37.46 -0.999 -0.999 GenAOB Plasmid mixes Soil DNA samples -3.35 -3.43 98.8 95.6 38.82 39.08 -0.994 -0.999 377 378 379 380 381 382 383 384 385 386 387 388 389 390 391 392 393 394 395 18 Intercept R2 Primer set 396 Supporting figure legends 397 398 Figure S1. An alignment of the GenAOA primer set (reverse complement of GenAOAR shown) 399 and 36 extended AOA amoA amplicons, representing the observed sequence diversity of a larger 400 set of sequences, shows variable positions within the priming region and intentionally-selected 401 nucleotide mismatches in the final primer design. For a) the forward primer, a variant including 402 a G nucleotide at the position indicated with a “1,” and for b) the reverse primer, three variants 403 including a T, G, or T at the position indicated with a “1,” “2,” or “3,” respectively, were 404 designed to attempt to further improve differential amplification of sequence variants with 405 multiple mismatches. Empirical testing via qPCR yielded inferior results (higher differential 406 amplification of sequence variants) compared with the final primer designs reported. 407 408 Figure S2. The extended-length (660 bp) AOA amoA amplicon used as a standard in qPCR 409 assays had the fewest number of mismatches for all primer sets. Mismatches within each primer 410 to the standard sequence are highlighted in color, while degeneracies are highlighted gray. 411 412 Figure S3. The average bacterial amoA gene count amplified from different ratios of Nsp 413 briensis and Nm europaea was significantly affected by the primer set. The GenAOB primer set 414 under-amplified Nm. europaea genes, while the RottAOB primer set slightly over-ampilfied 415 them, compared with the count produced using the TOPO primer set (range indicated by 416 horizontal gray bar). Data are means with range. 417 19 418 Figure S4. Archaeal amoA qPCR product generated from soil DNA using the a) GenAOA, b) 419 FranAOA, c) TreuAOA, and d) MincAOA primer sets visualized on a 2% agarose gel, 120 v for 420 45 min, stained with SYBR Safe DNA Gel Stain. In all gels, lane 1: 100 bp ladder, lane 2: 1 x 421 103 standard plasmid copies product, lanes 3-5: PR1-3 sample product, lanes 6-7: PAT1-2 422 sample product, lane 8: Boardman, WA soil DNA sample product (not discussed herein), lanes 423 9-11: OM1-3 sample product, lane 12: negative control, lane 10: 1,000 bp ladder. 424 425 Figure S5. Bacterial amoA qPCR product generated from single plasmids and plasmid mixtures 426 using the RottAOB and GenAOB primer sets visualized on a 2% agarose gel, 120 v for 45 min, 427 stained with SYBR Safe DNA Gel Stain. Lane 1 is 100 bp ladder, lanes 2-7 are product with the 428 RottAOB primer set, and lanes 9-14 are product with the GenAOB primer set. Products from 429 both primer sets follow the same order: 1 x 103 standard plasmid copies product, 100% Nsp 430 briensis, 100% Nm europaea, 20:80 Nm europaea:Nsp briensis, and 80:20 Nm europaea:Nsp 431 briensis (single and mixed plasmids that correspond to data in Figure S3), negative control. 432 433 Figure S6. Bacterial amoA qPCR product generated from soil DNA using the a) GenAOB and b) 434 RotthAOB primer sets visualized on a 2% agarose gel, 120 v for 45 min, stained with SYBR 435 Safe DNA Gel Stain. In both gels, lane 1: 100 bp ladder, lane 2: 1 x 103 standard plasmid copies 436 product, lanes 3-5: PR1-3 sample product, lanes 6-7: PAT1-2 sample product, lane 8: Boardman, 437 WA soil DNA sample product (not discussed herein), lanes 9-11: OM1-3 sample product, lane 438 12: negative control, lane 10: 1,000 bp ladder. 439 440 20 441 442 443 444 Figure S1. 445 446 447 448 449 450 451 452 21 453 454 455 Figure S2. 456 457 458 459 460 461 462 463 22 464 465 466 Figure S3. 467 468 469 470 471 472 473 474 475 476 477 478 479 480 23 481 482 483 484 Figure S4. 485 486 487 488 489 490 491 492 493 494 495 496 24 497 498 499 Figure S5. 500 501 502 503 504 505 506 507 508 509 510 511 512 513 514 515 25 516 517 518 Figure S6. 519 520 26