Decline-diseases are complex and becoming increasingly problematic to tree health globally. Acute Oak Decline (AOD) is characterized by necrotic stem lesions and galleries of the bark-boring beetle, Agrilus biguttatus, and represents a serious threat to oak. Although multiple novel bacterial species and Agrilus galleries are associated with AOD lesions, the causative agent(s) are unknown. The AOD pathosystem therefore provides an ideal model for a systems-based research approach to address our hypothesis that AOD lesions are caused by a polymicrobial complex. Here we show that three bacterial species, Brenneria goodwinii, Gibbsiella quercinecans and Rahnella victoriana, are consistently abundant in the lesion microbiome and possess virulence genes used by canonical phytopathogens that are expressed in AOD lesions. Individual and polyspecies inoculations on oak logs and trees demonstrated that B. goodwinii and G. quercinecans cause tissue necrosis and, in combination with A. biguttatus, produce the diagnostic symptoms of AOD. We have proved a polybacterial cause of AOD lesions, providing new insights into polymicrobial interactions and tree disease. This work presents a novel conceptual and methodological template for adapting Koch’s postulates to address the role of microbial communities in disease.
Trees are essential to landscape function and aesthetics, supporting diverse ecologies (Rackham, 2008) and providing key ecosystem services (Boyd et al., 2013). However, significant areas of forest have been lost due to increasing outbreaks of disease and pest attack, and tree health is a current global concern (Cohen et al., 2016). Tree diseases, including decline-diseases, are rising in profile due to an increased risk of introduction and spread through international plant trade and amplification effects of current and future climate change (McDowell et al., 2011; Oliva et al., 2014; Millar and Stephenson, 2015). Emerging evidence suggests that complex biotic interactions, including polymicrobial and insect activity, affect disease occurrence and severity (Adams et al., 2013; Buonaurio et al., 2015; Lamichhane and Venturi, 2015), yet little progress has been made in applying the latest advances in sequencing and culture-based methodologies to characterize pathosystems in trees. The prevailing paradigm of infection biology contends that one organism causes one disease (proved using Koch’s postulates). In contrast, there is increasing recognition of the importance of polymicrobial interactions in human disease, following developments in sequencing technologies that allow microbiome-wide association studies to identify the role of microbial communities in disease (Gilbert et al., 2016). In the medical field, this is leading to adaptations of Koch’s postulates to include complex interactions between the environment, host and microbial communities (Hill, 1965; Falkow, 1988; Fredricks and Relman, 1996). However, progress in characterizing polyspecies interactions in plant disease has been limited, although there is clearly a need for contemporary approaches to investigating complex tree diseases (Lamichhane and Venturi, 2015). Analysis of such complex biotic interactions requires an integrated, systems approach, particularly in the case of decline-diseases where both complex abiotic and biotic interactions underpin disease development.
Decline-diseases, first formally described as a specific disease in the United States (Sinclair, 1965; Manion, 1981) but well documented elsewhere (Delatour, 1983; Sinclair and Lyon, 2005; Thomas, 2008) are of global concern (Pautasso et al., 2015). Unlike most common tree diseases, decline-diseases are not caused by single primary pests or pathogens; instead they are complex syndromes, involving the sequential, combined and cumulative effects of (often secondary) biotic and abiotic agents (Manion, 1981; Thomas, 2008; Sallé et al., 2014; Brown et al., 2016). Currently, the United Kingdom is facing an episode of Acute Oak Decline (AOD), which occurs widely in southern and midland England, extending into Wales (Brown et al., 2016; Denman et al., 2016), and represents a significant threat to oak, particularly native species Quercus robur and Quercus petraea (Denman et al., 2014). First recognized in Britain in the 1980s (Denman and Webber, 2009), similar declines have occurred in continental Europe (Hartmann et al., 1989; Gibbs and Greig, 1997; Biosca et al., 2003; Vansteenkiste et al., 2004). AOD-affected trees show distinctive, weeping stem patches (stem bleeds), signifying areas of necrosis and fluid-filled cavities in the underlying inner bark (Denman et al., 2014) (see Figures 1a–c), which disrupt vascular flow of nutrients and water essential to tree survival (Vansteenkiste et al., 2004). Larval galleries of the buprestid beetle Agrilus biguttatus are found in conjunction with lesions (Brown et al., 2015, 2017) (Figure 1d) and can also impact tree condition by girdling the tree when colonization is intense, leading to tree death (Sallé et al., 2014). AOD typically affects mature oaks but has also been reported in young trees (Brown et al., 2016).
First steps to determine the causes of stem bleeds led to the isolation of several novel bacterial species from AOD lesions, with three novel species, Gibbsiella quercinecans (Enterobacteriaceae) (Brady et al., 2010), Brenneria goodwinii (Pectobacteriaceae) (Denman et al., 2012; Adeolu et al., 2016), Rahnella victoriana (Yersiniaceae) (Brady et al., 2014; Adeolu et al., 2016), and an unnamed Pseudomonas (Denman et al., 2016; Sapp et al., 2016) consistently isolated. Some of these species, for example, G. quercinecans as Serratia sp. (Biosca et al., 2003; Poza-Carrión et al., 2008) on Quercus pyrenacia and Quercus ilex are implicated as causative agents of stem bleeding on other oak species in Europe (Biosca et al., 2003; Poza-Carrión et al., 2008; Denman et al., 2016). There was less consistent isolation of various other bacterial species, for example, Lonsdalea quercina ssp. britannica (Brady et al., 2012), which is closely related to Lonsdalea quercina ssp. quercina, the causative agent of acorn gummosis on Q. agrifolia and Q. wislizenii in America (Hildebrand and Schroth, 1967), and several other novel species that are in the process of being formally described. Although correlation of certain bacterial species with AOD symptomology has been observed, empirical evidence on the causative agent(s) of AOD lesions is lacking and remains a barrier to developing informed management strategies for this disease. In the absence of a single putative primary pathogen as the causal agent of AOD lesions, we hypothesized that a polymicrobial complex is responsible for AOD lesion formation. However, demonstrating causation by a polymicrobial complex with associated insect activity on mature oak trees or logs is challenging in the context of fulfilling Koch’s postulates and requires a multi-faceted methodological and conceptual approach.
Here we applied a systems-level approach to determine cause(s) of necrosis in AOD using microbial isolation and culture, phenotypic tests, genomic analyses of G. quercinecans, B. goodwinii and R. victoriana, metagenome and metatranscriptome analysis of healthy and diseased trees and inoculation tests comprising both polybacterial inoculations and the addition of live A. biguttatus eggs to recreate the symptoms of AOD. This combined sequencing and cultivation-based approach provides a contemporary adaptation of Koch’s postulates to address the biotic components of a complex decline-disease and represents a conceptual model for future analyses of polymicrobial infections in trees and other systems.
Isolation of bacteria from healthy and diseased oak trees
In the search for putative causal agents of stem lesions, we wanted to determine the veracity of differences in occurrence and composition of bacterial communities in lesions and visually healthy trees, as the bacterial microbiome has previously been identified as the likely causal agent of stem lesions (Denman et al., 2016). Conventional isolation and culture and microbiome analyses were used. Samples were acquired through citizen science reports (CSR), as well as structured studies (Denman et al., 2016; Sapp et al., 2016) ensuring the broadest possible coverage of AOD sites (Supplementary Table S1 and S2). Eighteen CSR sites were sampled (Supplementary Figure S1 and Supplementary Table S1), together with those from structured studies (Denman et al., 2016; Sapp et al., 2016), as well as five sites that had no history of AOD (N-AOD). Trees were sampled by forest pathologists who made site visits following the enquiry. In total, isolations from 66 trees were analysed. Destructive sampling of trees, by removing panels of diseased oak tissue, as well as healthy oak tissue from apparently healthy trees on the same sites, was carried out where permitted, and isolations were made using PYGA medium as described in Denman et al. (2014, 2016) and Sapp et al. (2016). Owing to the nature of the CSR studies, the number of tissue pieces plated out was variable, dependent upon the sample. Bacterial colonies emerging from chips of tissue were purified using standard streak-plating techniques; single visually representative colonies were selected, cultivated in Luria Bertani broth (LB) and identified with PCR and DNA amplicon sequencing as described in Denman et al. (2016).
Statistical analysis of isolation study data sets
Bacterial yield between healthy and diseased trees was tested by fitting a generalized linear mixed-effects model with logit link function and binomial error distribution. Fixed effects were fitted for tree health and tissue position and random effects fitted for sites and trees within sites. Overdispersion in the model was taken into account by including an additional dispersion parameter.
Differences in bacterial communities were analysed by detrended correspondence analysis, down weighting bacterial species occurring in <5% of tissue combinations. Monte Carlo permutation tests were used to test for significant differences in bacterial communities between healthy and diseased trees and to test the effect of tissue position within the tree. Finally, Jaccard’s similarity index was used to identify any significant associations between bacteria across the 66 trees of the study.
Genome sequencing of bacterial strains isolated from AOD-affected trees
Maintenance of bacterial strains used in genome analyses
G. quercinecans FRB97 (T) (Brady et al., 2010), B. goodwinii FRB141 (T) (Denman et al., 2012) and R. victoriana BRK18a (T) (Brady et al., 2014) were isolated by Forest Research in the CSR studies from oak trees affected by AOD. Strains were stored in glycerol stocks at −80 °C and maintained on nutrient agar (Oxoid, ThermoFisher Scientific, Loughborough, UK) at 20 °C.
DNA preparation and genome sequencing on Pacific Biosciences RSII sequencing platform
The whole genomes of G. quercinecans FRB97, B. goodwinii FRB141 and R. victoriana BRK18a were sequenced using the Single Molecule Real-Time (SMRT) technology of the Pacific Biosciences RSII platform. A single colony of each isolate was sampled from nutrient agar (Oxoid) and used as inoculum for liquid culture, which was grown overnight in nutrient broth (Oxoid) at 28 °C, and shaken at 150 r.p.m. Total genomic DNA was isolated using the Gentra Puregene Yeast/Bact. Kit (Qiagen, Manchester, UK) and quantified using a Qubit fluorometer (Life Technologies, Paisley, UK). DNA integrity was assessed using 1% agarose gel electrophoresis. G. quercinecans and B. goodwinii DNA libraries were prepared using 10 μg of genomic DNA and sequenced by DUGSIM at Duke University, NC, USA, using P4/C2 chemistry and six SMRT cells per isolate. The R. victoriana DNA library was prepared and sequenced by the Centre for Genomic Research, University of Liverpool, UK using P6/C4 chemistry and one SMRT cell. All sequence data described in this study are available under BioProject PRJNA323828, (Supplementary Table S3). Genome assembly and annotation are described in Supplementary Methods.
Metagenome sequencing of diseased and healthy oak trees
Collection of samples for metagenome sequencing
Tissue samples were collected from Runs Wood, Ross-on-Wye and two sites in Attingham park (Supplementary Table S2). More than half of the trees sampled for metagenome analysis were also sampled in the isolation study. A panel comprising all layers of stem tissue (outerbark, innerbark, sapwood and heartwood) was removed from the visible bleed area on each diseased tree or from stem areas at similar height on healthy trees according to previously described methods (Denman et al., 2014, 2016; Sapp et al., 2016). Samples were immediately flash frozen on dry ice and stored at −80 °C prior to processing.
Metagenome assembly, annotation and mapping to the genomes of G. quercinecans FRB97 (T), B. goodwinii FRB141 (T) and R. victoriana BRK18a (T)
Metagenomic reads were assembled using RAY-meta v2.3.1 (Boisvert et al., 2012) using default parameters. Assemblies were annotated using Prokka v1.11 (Seemann, 2014). Translated annotations were aligned against the translated protein sequences of G. quercinecans FRB97 (T), B. goodwinii FRB141 (T), R. victoriana BRK18a (T) and two control genomes Pectobacterium carotovorum ssp. carotovorum PC1 and Paenibacillus polymyxa SC2 using BLASTx v2.2.26 (Altschul et al., 1990). Metagenome sequences with >97% homology for at least 50 amino acids to proteins identified in G. quercinecans, B. goodwinii and R. victoriana were considered a match (Supplementary Table S4). Control genomes were selected to measure the stringency of alignment. P. carotovorum ssp. carotovorum is a canonical plant pathogen and a member of the soft-rot Enterobacteriaceae (SRE) (N.B. many members have recently been reclassified into novel families (Charkowski et al., 2012; Adeolu et al., 2016)), which had been identified sporadically and at low relative abundance from metagenomic taxonomic surveys within this study (Supplementary Table S5). However, P. carotovorum ssp. carotovorum had not previously been isolated from necrotic lesions on AOD-affected trees. Therefore, it was proposed that coding domain alignments to P. carotovorum ssp. carotovorum align to conserved genes, which are present in many Enterobacteriaceae, and their low relative abundance does not signify their presence but is an artefact of the alignment process. Resultant Circos plots agree with this proposal as conserved genes are frequently found in the metagenomic alignment against the P. carotovorum ssp. carotovorum PC1 genome, which are likely to align to other Enterobacteriaceae. Within G. quercinecans, B. goodwinii and R. victoriana, there is strong homology to conserved and variant genes. P. polymyxa SC2 was identified at low relative abundance in healthy and diseased metagenomic samples (Supplementary Table S5), therefore it was selected to test stringency of the metagenomic alignment and to measure its relative abundance in healthy and diseased microbiomes using an alternative method. Homologous bacterial protein identities and the workflow used for metagenomic analysis is available from GitHub: (https://github.com/clydeandforth/multi_omics_study.git).
Taxonomic classification of metagenome sequences
To compare the taxonomic composition of the oak microbiome, raw sequence reads were taxonomically labelled using Kraken v0.10.5 beta (Wood and Salzberg, 2014) and One Codex (Minot et al., 2015) (Figure 2a). Taxonomic labelling using Kraken was performed on the standard RefSeq genome database supported by Kraken, with the addition of the genomes of B. goodwinii FRB141 (T), R. victoriana BRK18a (T), G. quercinecans FRB97 (T) and Lonsdalea quercina ssp. quercina ATCC 29281 (Figure 2d and Supplementary Table S5). Taxonomic analysis using One Codex was conducted against the One Codex March ’16 Preview database with the addition of the genomes of G. quercinecans, B. goodwinii and R. victoriana.
Functional annotation of metagenome sequences
Metagenome datasets derived from samples AT2, AT3, AT4, AT5, AT6, ROW1, ROW2 and ROW3 were analysed via MG-RAST (Meyer et al., 2008) using Hierarchical Classification against the Subsystems database with an E-value cutoff of 1e-5, a minimum percentage identity cutoff of 80% and a minimum alignment length of 50. Descriptions of the taxonomic and functional composition of the metagenomes derived from MG-RAST were comparable with those derived from analysis of the same data sets using One Codex and Kraken and further validated by mapping of metagenome reads against the finished genomes of B. goodwinii, G. quercinecans and R. victoriana.
Statistical analysis of metagenome data sets
Statistical analyses were performed using Primer v7 (Clarke and Gorley, 2015) with PERMANOVA+ add on to explore relationships between community changes (Figure 2b). One Codex metagenome data was log (N+1) transformed to downweight the most abundant genera. Next, dissimilarities were calculated with the S17 Bray–Curtis similarity coefficient. A principal coordinate ordination analysis was performed by plotting the interpoint dissimilarity values for each factor (site and disease status), and the variation in community composition was plotted as the first two axes (preserving actual dissimilarities) (Gower, 1966). A correlation was performed between each taxon and each community coordinate. Correlations with each component were deemed significant (R2>0.5) and a vector biplot was overlaid to visualize the strength of the correlation. A Welch’s t-test was performed to test significance of differences between key taxa (identified above) and between healthy and diseased trees (pooled abundances for each factor). Resultant P-values from Welch’s t-test are overlaid on correlation biplot with significance at >95% (P<0.05) deemed significant. Comparative functional analysis of MG-RAST (Meyer et al., 2008) annotated, metagenome data was performed using Stamp v2.1.3 (Parks et al., 2014). Statistically significant functional differences between diseased and healthy communities were calculated using G-test with Yates’ correction. The Newcombe–Wilson test was performed to calculate confidence intervals between two binomial population proportions (Brown and Li, 2005).
Metatranscriptome sequencing of AOD diseased oak trees
Collection of samples for metatranscriptome sequencing and RNA extraction
For RNA sampling, two separate lesions (samples AT11 and AT12) from a single tree were analysed in June 2013. Swabs of the lesion fluid were collected in addition to tissue from the active margins of the lesion and immediately frozen in liquid nitrogen and transported back to the laboratory in a vessel containing liquid nitrogen. Samples were stored at −80 °C prior to processing. Before RNA extraction, samples in liquid nitrogen were ground with a pestle in a mortar to homogenize the tissue. RNA was extracted from 2 g of tissue using the PowerSoil Total RNA Isolation Kit (MoBio, Cambridge, UK) according to the manufacturer’s instructions. RNA was quantified using a Qubit fluorometer (Thermo Fisher, Warrington, UK) and quality assessed using the Bioanalyser 2100 (Agilent, Manchester, UK).
Sequencing libraries were prepared from samples of total RNA using the strand-specific ScriptSeq Preparation Kit (Illumina, Cambridge, UK) and sequenced using 2 × 100 bp paired-end sequencing on the Illumina HiSeq platform. Reads were trimmed using first Cutadapt 1.2.1 (Martin, 2011) and additionally Sickle 1.2.00 (Joshi and Fass, 2011). Owing to low RNA yields from the lesion samples, total RNA was sequenced and rRNA sequence reads were subsequently depleted in silico prior to mRNA transcript analysis.
Metatranscriptome assembly and functional annotation
Two in silico rRNA-depleted metatranscriptome libraries were aligned to the G. quercinecans FRB97 (T), B. goodwinii FRB141 (T), R. victoriana BRK18a (T) and control genomes (P. carotovorum ssp. carotovorum PC1 and P. polymyxa SC2) (Supplementary Figures S2 and S3) with Bowtie2 v2.2.4 (Langmead and Salzberg, 2012), using local mode to maximize alignment score. Aligned reads were converted from Sequence Alignment/Map (SAM) to Binary Sequence Alignment/Map (BAM) format and indexed using SAMtools v1.2 (Li et al., 2009). To avoid false positives in the detection of gene expression, a gene was considered as being expressed if 3 transcripts were aligned and the combined coverage from both libraries represented >20% of the gene, (adapted from (Versluis et al., 2015) (Figures 2a–c and Supplementary Figure S4). A custom Perl script was designed to extract transcript alignments and is available from GitHub: (https://github.com/clydeandforth/multi_omics_study.git). Aligned transcripts were visualized in Artemis (Carver et al., 2012).
Pathogenicity tests were set up to reproduce lesions characteristic of AOD under controlled conditions. The following hypotheses were tested: (1) Key species consistently isolated from AOD symptomatic oak can cause necrosis of oak stem tissue, (2) Combinations of key bacterial species cause more severe tissue necrosis (reflected in larger lesions), than individual species alone, and (3) The interaction between A. biguttatus larvae (derived from eggs) and bacteria leads to the development of AOD symptoms.
Four experiments were carried out over 3 consecutive years as testing could only be carried out annually when beetle eggs were available. Three trials were carried out on oak logs in growth chambers, and the fourth trial was set out in the field, where stems of young plantation-oak (25 years old), were used instead of logs.
Growth chamber log trials
Logs used in the trials were obtained from freshly felled Q. robur trees, with diameter at 1.3 m (DBH)=16–20 cm. The trees were located in the Straits Enclosure of the Alice Holt Forest, Hampshire, England, UK, and logs were transported to the laboratory after felling where they were prepared for inoculation. Logs measuring 40 cm (mini-logs) or 130 cm (long logs) in length had the uppermost cut surface sealed with isoflex liquid rubber (Ronseal Ltd, Chapeltown, Sheffield) to prevent desiccation. Logs were placed, lower cut surface down, in saucers containing water. Logs were inoculated in August or September and incubated at 25 °C in the growth chamber with a 12 h photoperiod. Mini-logs were used for all treatments involving A. biguttatus eggs; in each case, only one bacterial+eggs treatment type per mini-log was tested to guard against cross-contamination through larval spread (Supplementary Table S2). All the bacterial treatments without eggs (either single species or combinations of species) were placed on the same long log, with inoculation points marked out along its length. Eggs of A. biguttatus were produced in Forest Research’s laboratories at Alice Holt (Reed, 2016). In a single experiment (2014 NW; Supplementary Table S2), non-wound inoculations were carried out; the remaining two growth chamber trials and the field trial were inoculated using shallow wounds to the outer surface of the innerbark, made by a 10 mm cork-borer. Half a loop of inoculum scooped from 24-h-old inoculum plates using disposable plastic loops was inserted into the wound and rubbed to dislodge the bacterial cells around the wound surface. The outer bark plug was replaced on the inoculation point, wounds covered with parafilm and damp cotton wool and sealed with duct tape. After 4 months of incubation, experiments were terminated, outer bark stripped from inoculation points to expose lesions, which were hand traced onto tracing paper, and back isolations were cultured onto peptone yeast glucose agar. Mass bacterial colonies that developed were tested for the presence of B. goodwinii, G. quercinecans, Rahnella and Lonsdalea using a multiplex Taqman qPCR assay (Roche, Brighton, UK). Lesion areas were calculated using ASSESS V2 (APS, Minneapolis, MN, USA).
Log lesion areas
The four pathogenicity trials were used to establish the impact of different bacterial species tested individually, in combination (polybacterial inoculations) and with or without the addition of A. biguttatus eggs (Supplementary Table S2) on tissue necrosis (assessed by the size of the lesion area associated with each inoculation point).
Lesion area data were refined in a hierarchical manner, such that the following data sets were used for lesion area analysis:
Non-contaminated samples fulfilling Koch’s postulates, with galleries present (for A. biguttatus samples indicating that eggs had hatched);
Non-contaminated samples fulfilling Koch’s postulates, with or without galleries present (for A. biguttatus samples); and
Further information on statistical analyses of log lesion areas are described in Supplementary Methods.
In the isolation study, analysis of 38 diseased trees from 23 sites, plus 13 healthy trees in 11 of these sites, and 15 healthy trees from five sites with no history of AOD identified 159 bacterial taxa. Higher yields of bacteria were obtained from lesion margin tissue of symptomatic trees compared with healthy tree tissue (F1,28, P<0.001), and the lesion margin bacterial profile was significantly different to healthy tissues (Monte-Carlo permutation test of 1000 permutations, P<0.001) (Supplementary Figure S5 and Supplementary Table S6). Key genera isolated included Pseudomonas (comprising multiple taxa and occurring in healthy as well as diseased trees); but Gibbsiella, Brenneria and Rahnella dominated lesion margins (Supplementary Table S6). G. quercinecans occurred on all disease sites and was isolated from 83% of diseased and 4% of healthy trees sampled, comprising 17% of total diseased samples and <0.1% of total healthy samples. B. goodwinii was more difficult to isolate but was obtained from 15 sites, accounting for 16% of total diseased and <0.1% of total healthy samples. Members of the genus Rahnella were obtained from 65% of diseased sites, but R. victoriana was isolated only from diseased trees (37%), on nine of the sites. L. quercina ssp. britannica (Brady et al., 2012) was isolated sporadically on four sites, and a Pseudomonas species (P. fulva-like) not yet formally identified, was isolated at eight sites from diseased trees only (Supplementary Table S6). There was a significant co-occurrence of G. quercinecans and B. goodwinii in diseased tissue (J=0.56, P<0.001), but neither was isolated from trees on sites with no history of AOD.
Oak microbiome analysis
Taxonomic analysis of the metagenome using unassembled metagenome sequence reads against the One Codex (Minot et al., 2015) March ’16 Preview database (with the addition of the genomes of G. quercinecans, B. goodwinii and R. victoriana) also revealed a shift in microbiome composition between healthy stem tissue and AOD lesions (Figures 2a and b). Periglandula, Burkholderia, Streptomyces, Bacillus and Auriemonas were the most abundant genera in healthy trees, whereas Brenneria dominated diseased tissue (mean read abundance, 37.5%) (Figure 2a). The mean read abundance of Gibbsiella (0.9%) and Rahnella (3.7%) was also greater in diseased tissue when compared with healthy tissue (both 0.1%). Pseudomonas, a diverse genus comprising both endophytic and phytopathogenic bacteria (Vinatzer et al., 2014), had similar mean abundances in both diseased (4.8%) and healthy trees (3.3%). Correlation coefficients and Welch’s unequal variances t-tests revealed that Streptomyces (tWelch’s=49.7, P=0.004) and Periglandula (tWelch’s=821.8, P<0.001) were significantly associated with healthy trees, whereas Brenneria (tWelch’s=12.4, P=0.006) and Gibbsiella (tWelch’s=4.7, P=0.05) were strongly correlated with the lesions of diseased trees (Figure 2b and Supplementary Table S7). Pseudomonas and Rahnella were not strongly correlated with either health state (Supplementary Table S7).
To identify the most abundant species in the lesion microbiome, raw metagenome reads were aligned using Kraken (Wood and Salzberg, 2014) against reference genome databases (see Methods section), revealing 17 genomes that were commonly detected in diseased tissue (Figure 2d and Supplementary Table S7). B. goodwinii, G. quercinecans and R. victoriana were detected in the lesion metagenome of all trees with AOD. Overall, B. goodwinii was the most abundant genome in the lesion microbiome (range, 0.3–49% of metagenome sequence reads; mean, 12%) but was also detected in much lower proportions in healthy trees (0.01% in all samples). R. victoriana (range, 0.01–15%; mean, 2.1%) and G. quercinecans (range, 0.02–0.8%; mean, 0.3%) were the second and fourth most abundant genomes in the lesions of diseased trees, respectively. Functional metagenome analysis (Figure 2c and Supplementary Figure S6) revealed that genes associated with carbohydrate metabolism, membrane transport and virulence, defence and disease are key features of the lesion microbiome, suggesting that many of these functions are encoded in the genome of B. goodwinii, G. quercinecans and R. victoriana.
Genome analysis of AOD-associated bacteria
Whole-genome sequencing of B. goodwinii FRB141, G. quercinecans FRB97 and R. victoriana BRK18a (Supplementary Table S8) revealed that they are phylogenetically related to opportunistic phytopathogens belonging to the SRE (Charkowski et al., 2012; Adeolu et al., 2016) and possess a catalogue of virulence genes associated with canonical phytopathogens (Supplementary Table S9). The SRE alternate their lifestyle from benign commensals to brute force necrotrophic pathogens, which macerate cell wall polysaccharides by releasing plant cell wall-degrading enzymes (PCWDEs) (Toth et al., 2006). A genome-wide search for PCWDEs in G. quercinecans, B. goodwinii and R. victoriana revealed the presence of pectinases, cellulases and tannases (Figure 3b, Supplementary Table S9) whose activity has been confirmed phenotypically (Supplementary Figure S7). Furthermore, G. quercinecans and R. victoriana possess a type II secretion system, an operon which releases most PCWDEs and is therefore the central virulence facilitator of necrotrophic plant pathogens. B. goodwinii encodes a type III secretion system, the principal virulence factor of established hemibiotrophic pathogens such as Pseudomonas syringae, which use the operon to evade immune surveillance, allowing bacteria to increase their numbers before releasing necrotic enzymes as nutrients are depleted (Tampakaki et al., 2010).
To address the role of B. goodwinii, G. quercinecans and R. victoriana in the aetiology of AOD, we aligned metagenome sequences and transcripts recovered from necrotic lesions of AOD-affected trees against their genomes (Figure 3a). Alignment of six AOD lesion metagenomes revealed an average of 2225 homologous proteins in B. goodwinii FRB141, 858 in G. quercinecans FRB97 and 396 in R. victoriana BRK18a (Supplementary Table S4). Furthermore, annotated genes from the assembled metagenome of a healthy oak revealed only two homologous proteins in B. goodwinii FRB141, one in G. quercinecans FRB97 and two in R. victoriana BRK18a. Lesion transcripts were aligned to coding regions within B. goodwinii FRB141, G. quercinecans FRB97 and R. victoriana BRK18a; this revealed that the transcripts aligned significantly to virulence genes, including PCWDEs, secretion system machinery and regulators of PCWDEs (Figure 3c and Supplementary Figure S4). G. quercinecans FRB97 expressed the pectic enzymes, polygalacturonase and rhamnogalacturonate lyase, and β-glucosidase (cellulase), pectate exo-lyase and oligogalacturonide lyase (which cleaves polygalacturonic acid, the by-product of pectin lyase) (Moran et al., 1968). B. goodwinii FRB141 expressed phosphocellosbiose, β-galactosidase and several type III secretion system effectors, R. victoriana BRK18a expressed many general secretory pathway genes, a β-glucosidase, a tannase and carbohydrate esterase enzyme (Yao et al., 2013). Key regulators of pectinolysis were expressed in all three bacteria, including kdgR, phoP, pecT, rsmA/rsmB and gacA (Figure 3a).
Log lesion areas
Figures 1e–l show lesions caused by bacteria with or without A. biguttatus inoculated into logs in pathogenicity tests. Notable results for lesion area analysis are presented in Figures 1m and n (non-contaminated samples fulfilling Koch’s postulates, with galleries present for A. biguttatus samples). In bacteria-only inoculations, lesions significantly bigger than wound controls (Figure 1m) were made by the combination of bacterial species B. goodwinii+G. quercinecans (tdunnetx=2.97, P=0.044); the bacterial species G. quercinecans had larger lesion areas versus the controls, although this was not significant and the P<0.05 level (tdunnetx=2.79, P=0.068); B. goodwinii lesions were smaller and not significantly different from the controls in terms of mean lesion area (tdunnetx=1.30, P=0.796), but the necrosis was clearly different to the control wound response (see Figure 1e vs f). Inoculation with Erwinia billingiae, a known ubiquitous non-pathogenic bacterium, served as a negative control demonstrating lesion area no different to the control wound response. The pattern strengthened when bacteria plus A. biguttatus (applied as eggs) were co-inoculated (Figure 1n). Lesions created by B. goodwinii and A. biguttatus eggs (larvae) were significantly bigger than wound controls (tdunnetx=3.40, P=0.0125), as were G. quercinecans and A. biguttatus (tdunnetx=4.65, P=0.0002) and the combination of B. goodwinii+G. quercinecans+A. biguttatus (tdunnetx=3.92, P=0.0027) (Figure 1n). Bacteria were re-isolated from lesion margins and at intervals along the larval galleries, which were becoming necrotic-forming part of the lesion. Apart from demonstrating the necrogenic ability of the bacteria, these results showed that the larvae and larval galleries have an important part in increasing lesion area, implicating them in the spread of bacteria within infected trees.
Bacterial-positive back-isolation and A. biguttatus contamination
There was a high success of back-isolation for both B. goodwinii and G. quercinecans when these species were included as treatments (70% and 80%, respectively); both species were also identified as contaminants (that is, back-isolated when not part of the treatment inoculation; B. goodwinii=9%; G. quercinecans=16%), although the contamination rate was significantly lower than treatment back-isolation in both cases (B. goodwinii: z=7.98, P<0.001; G. quercinecans: z=6.65, P<0.001). For G. quercinecans, the rate of contamination was affected by the presence of A. biguttatus eggs: when eggs were absent G. quercinecans contamination was 3%; when eggs were present this rose to 38% contamination, a significant increase (z=3.59, P<0.001). There was no significant effect of A. biguttatus eggs on B. goodwinii contamination (eggs absent, B. goodwinii contamination=2%; eggs present, B. goodwinii contamination=7%, z=1.60, P=0.11).
Fulfilling Koch’s postulates represents the traditional paradigm for proving disease causation. However, contemporary molecular approaches have transformed our appreciation of the role of microbial communities and polymicrobial interactions in disease. There are situations where the one pathogen causes one disease model is not suitable to prove causality and must be adapted to accommodate polymicrobial infections. For example, in decline-diseases of trees, application of Koch’s postulates in the strictest sense cannot fully address proving causality of lesion formation as more than one necrogenic agent is involved in the disease syndrome. Here causation of AOD lesions was demonstrated using a combined cultivation-based and sequencing approach in a dynamic adaptation of Koch’s postulates analogous to that described by Byrd and Segre (2016). Koch’s first postulate is fulfilled by the consistent isolation and metagenomic detection of G. quercinecans, B. goodwinii and R. victoriana in trees affected by AOD.
This combined approach delivered an improved understanding of lesion microbiome composition, as some species were difficult to isolate and culture. For example, B. goodwinii and Lonsdalea quercina ssp. britannica were under-represented, whereas G. quercinecans, which is more amenable to isolation and cultivation, was overrepresented, with the opposite trend evident in metagenomic studies. Furthermore, G. quercinecans, B. goodwinii and R. victoriana were absent on sites with no history of AOD, were rarely isolated from healthy oak on diseased sites and had negligible abundance in healthy metagenome samples at AOD sites, complying with Koch’s second postulate. Ultra-low levels of G. quercinecans, B. goodwinii and R. victoriana were detected in some of the healthy trees but only from sites where AOD is present, raising interesting questions about their existence in the wider environment. Possible explanations for the presence of G. quercinecans, B. goodwinii and R. victoriana in healthy trees on AOD sites may include; (1) the tree is in early stages of lesion formation, where visible symptoms have not yet developed, or that (2) G. quercinecans, B. goodwinii and R. victoriana are endophytes or epiphytes that opportunistically multiply after tissue necrosis is initiated by another organism. In the first situation, the chances of detecting asymptomatic lesion formation seem fairly remote, especially as crown condition is not a reliable indicator of tree predisposition status in the early stages of decline development. In the second case, several pieces of evidence counteract the possibility that these organisms multiply opportunistically after tissue necrosis occurs, as (1) we observed the expression of putative necrogenic enzymes and virulence factors of these bacteria in AOD lesions in planta, implicating them in having an active role in tissue degradation, and (2) G. quercinecans and B. goodwinii caused significant lesion formation in log inoculation trials, demonstrating actual lesion-forming capabilities. It is important to note that the oak logs and trees used in our trials were selected from areas with no history of the disease.
Furthermore, all three bacterial species possess the genomic capability to cause tissue necrosis, as determined through genomics, in situ functional metagenomics and metatranscriptomics. Inoculation onto live oak logs confirmed significant necrogenic ability of B. goodwinii and G. quercinecans, but further work with R. victoriana inoculation is required. Thus the pathogenic phenotype of B. goodwinii and G. quercinecans has been confirmed, broadly fulfilling Koch’s third postulate that inoculation tests can cause the disease anew. However, bacterial species combinations caused even greater necrosis indicating cumulative effect and possible synergism, this is a contemporary adaptation of Koch’s postulates sensu stricto. Finally, once inoculated onto live oak panels, B. goodwinii and G. quercinecans were re-isolated to fulfil Koch’s fourth postulate (although back-isolation of some species was difficult, and there is a need for developing rapid, cost-effective tools to detect pathogens that are difficult to isolate). Consequently, we propose that the biotic component of the AOD lesions is a polybacterial complex comprised primarily of G. quercinecans and B. goodwinii, which are now established as key causal agents of tissue necrosis, the primary symptom of AOD. Our studies also indicated that other members of the microbiome may contribute to the pathology of AOD. Microbiome analysis suggested that R. victoriana is abundant and also important in AOD lesions; however, back-isolation of R. victoriana was variable, and further tests to characterize its role and interactions with B. goodwinii and G. quercinecans are required. In addition, Lonsdalea quercina ssp. britannica in particular demonstrated variable but at times virulent pathogenicity in log inoculations, although it was not consistently present in AOD lesions. Our results indicate that Agrilus larvae potentiate the spread of these necrogenic bacterial species within tree tissue, generating new break-out points of tissue necrosis and replicating the observed aetiology of AOD. Ultimately, vascular degradation arising from a combination of bacterial tissue necrosis and inner bark damage from larval galleries exacerbates and accelerates the decline by interrupting carbon resource allocation, preventing accumulation in roots and reducing water availability.
It is clear that, where possible, microbiome analysis methods together with inoculation assays should become the accepted standard for profiling disease complexes, particularly when considering complex interactions between microorganisms, insects, the environment and the host. This phenomenon has never previously been addressed in arboreal systems using the approaches described here. Our work therefore highlights the importance of a systems-level approach for characterizing the pathology of complex diseases and represents a conceptual and methodological template for adapting Koch’s postulates to address the role of microbial communities in disease. In recent years, microbiome studies have transformed our understanding of the role of human gut microbiota in a variety of conditions, including bowel and cardiovascular disease (Frank et al., 2007; Koeth et al., 2013), and consequently, microbiome-wide association studies that link microbial consortia to disease will have an important role in the development of future diagnostics and therapies for disease (Gilbert et al., 2016). For decline-diseases in particular, further adaptation may be required to include the role of host predisposition.
Although AOD has been formally described as a major threat to UK oak, similar decline-diseases have been reported in mainland Europe (Delatour, 1983; Hartmann et al., 1989; Biosca et al., 2003; Vansteenkiste et al., 2004; Poza-Carrión et al., 2008), the Middle East and the Americas (Lynch et al., 2014), indicating that AOD is a global concern that has likely evaded attention due to the complexity of its causative agents. The polybacterial nature of AOD exhibits similarities to other economically important tree diseases such as olive knot disease (Buonaurio et al., 2015) but may also be applied to other complex diseases. Generally, our findings highlight the importance of understanding polymicrobial interactions in the context of future-proofing plant health to protect important but increasingly disease-prone forests and crops that are a fundamental part of our global landscape.
This work was supported by Woodland Heritage, the Rufford Foundation, the Monument Trust, the JPG fund, HPC Wales, the Forestry Commission and DEFRA (TH0108). We thank the private land owners, public forest estate, the National Trust and the Woodland Trust for site access and allowing tissue sampling of oaks. We also thank the internal reviewers for their helpful suggestions on the manuscript. Sequence data generated in this study are available under NCBI BioProject PRJNA323828 and PRJNA321868. We thank Katy Reed and Daegan Inward for supplying Agrilus egg and the Forest Research Technical Service Unit for supplying logs and assistance with field and log trials. We also thank Lucille Rainbow and Margaret Hughes of the Centre of Genomic Research for library preparation and sequencing.
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Supplementary Information accompanies this paper on The ISME Journal website (http://www.nature.com/ismej)
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