1 Supplementary Information 2 PCR cycling conditions 3 Each PCR reaction contained DNA (2 ng), 200 nM of each primer, 0.25 µl MyTaqTM DNA 4 polymerase (Bioline, Alexandria, Australia), 1 x of the supplied buffer, and 250 µM of each 5 dNTP. The cycling conditions used for 16S rRNA gene amplification were as follows: 94oC 6 for 2 minutes (one cycle), 98oC for 30s, 55oC for 30s, 72oC for 30s (28 cycles), and a final 7 extension step of 72oC for 10 minutes. Fungal ITS1 region was amplified using the same 8 conditions except that the annealing temperature used was 53oC. After amplification PCR 9 products were cleaned with Agencourt® AMPure® beads (Beckman Coulter, Lane Cove, 10 Australia) and quantified using Quant-iTTM Picogreen® dsDNA quantification kit (Life 11 TechnologiesTM, Mulgrave, Australia) according to the manufacturer’s instructions and DNA 12 concentration was normalised to 4 ng µl-1. 13 14 T-RFLP 15 Restriction digest were performed as follows: 25 ng of PCR product was added to a reaction 16 mixture containing sterile water, 20 units of restriction enzyme AluI (New England Biolabs, 17 Ipswich, MA) and 4 µl of the specified buffer. Reaction mixtures were incubated at 37°C for 18 3 hours and subsequently stored at 4°C. Digests were desalted by precipitation by incubation 19 with ice cold 150 µl of 75% isopropanol (Sigma-Aldrich, Sydney, Australia) (v/v) for 30 20 minutes followed by centrifugation at 4000 rpm for 45 minutes. Digested and purified PCR 21 products were re-suspended in nuclease-free sterile water. Digested PCR products were added 22 to a 10 µl reaction mixture containing 9.7 µl of M Hidi formamide and 0.3 µl of GeneScanTM 23 600 LIZ size standard (Applied Biosystems, Mulgrave, Australia) and denatured at 94°C for 3 1 24 minutes. Fragment lengths were determined by electrophoresis using an AB3031xl Genetic 25 Analyzer (Applied Biosystems). 26 27 T-RFLP data processing 28 Bacterial 16S rRNA gene T-RFLP profiles were processed by removing peaks smaller than 29 29 bp and larger than 500 bp. The Interactive Binner R script (Ramette 2009) was used to bin 30 the resulting fragments using a sliding window approach, with minimum and maximum size 31 cut-offs of 40 and 500 bp respectively, minimum RFI (relative fluorescence intensity) of 0.09, 32 a window size of 1.5 bp and a shift size of 0.15 bp. Fungal ITS T-RFLP profiles were treated 33 similarly except that minimum and maximum size cut-offs were 30 and 600 bp, and a window 34 size and a shift size of 1 and 0.1 bp were used respectively. T-RFLP analysis generated 35 profiles of the relative abundance of ribotypes per samples (ribotypes represent a unit of 36 microbial diversity obtained with T-RFLP corresponding to DNA fragments of specific size 37 resulting from endonuclease digestion of PCR products). 38 39 qPCR cycling conditions 40 Bacterial 16S rRNA gene and fungal ITS1 region were quantified in triplicate reactions 41 containing 1x SsoAdvancedTM SYBR® green Supermix (Bio-Rad, Hercules, CA), 400 nM 42 primers, 2 µl DNA (diluted 1 in 10) and H2O to 10 µl. Cycling conditions were as follows: for 43 16S rRNA gene, 95oC for 1 minute (one cycle), 95oC for 15s and 56oC for 20s (39 cycles); for 44 ITS1, 95oC for 1 minute (one cycle), 95oC for 5s and 53oC for 20s and extension at 72oC (39 45 cycles). A melt curve from 65oC to 95oC was added at the end of the amplification cycles. 46 Standards were run in triplicates in each qPCR plate with 10-fold dilution series from 108 to 2 47 100 copies µl-1 of purified PCR product from Pseudomonas fluorescens strain 5.2 or 48 Fusarium oxysporum vasinfectum. Amplification efficiencies were > 90% and R2 were > 0.99 49 for all bacterial and fungal calibration curves. 50 51 WCNA analysis 52 Weighted correlation network analysis was developed with the aim of reducing and 53 integrating highly dimensional data in order to allow more robust associations to be drawn 54 between biological and non-biological components of complex systems (Langfelder and 55 Horvath, 2008). To build the network, the absolute value of the correlation coefficient 56 between the abundance profiles of each ribotype was calculated, generating an abundance 57 profile similarity matrix. A soft-thresholding procedure was applied to the abundance 58 similarity matrix to calculate the adjacency matrix which expresses the connection strength 59 between the ribotypes. Scale-free topology is thought to be a universal property of modular 60 biological systems, as is the case of soil microbial communities (Barberán et al. 2012, Zhou et 61 al. 2011). The soft-thresholding procedure leads to an emphasis of stronger over weaker 62 connections between nodes (genes, OTUs or ribotypes) in order to detect robust, biologically 63 meaningful modules within the network (Langfelder and Horvath 2008). In WCNA, node 64 linkages vary continuously, and node membership in a module is also continuous, or fuzzy. 65 Weighted networks will therefore better represent biological processes that vary continuously 66 (Langfelder and Horvath, 2008). In WCNA-generated networks, modules are groups of nodes 67 (genes, OTUs or ribotypes) of strong topological overlap, which is interpreted as nodes that 68 co-correlate strongly (Yip and Horvath, 2007). The modules are detected using average 69 linkage hierarchical clustering coupled with topological overlap matrix (TOM) based 3 70 dissimilarity, and correspond therefore to branches in a node (OTUs, genes or ribotypes) 71 hierarchical clustering tree. 72 73 74 Supplementary references 75 Barberán A, Bates ST, Casamayor EO, Fierer N (2012). Using network analysis to explore co- 76 occurrence patterns in soil microbial communities. ISME Journal 6: 343-351. 77 78 Langfelder P, Horvath S (2008). WGCNA: an R package for weighted correlation network analysis. 79 BMC Bioinformatics 9: 559. 80 81 Ramette A (2009). Quantitative community fingerprinting methods for estimating the abundance of 82 operational taxonomic units in natural microbial communities. Applied and Environmental 83 Microbiology 75: 2495-2505. 84 85 Yip AM, Horvath S (2007). Gene network interconnectedness and the generalized topological overlap 86 measure. BMC Bioinformatics 8: 22. 87 88 Zhou J, Deng Y, Luo F, He Z, Yang Y (2011). Phylogenetic molecular ecological network of soil 89 microbial communities in response to elevated CO2. MBio 2: pii: e00122-00111. doi: 90 00110.01128/mBio.00122-00111. 91 4 92 Supplentary Figure legends 93 Figure S1: Map showing sampling locations 94 5