Genome of the Asian longhorned beetle (Anoplophora glabripennis), a globally significant invasive species, reveals key functional and evolutionary innovations at the beetle–plant interface
- Duane D. McKenna1, 2Email author,
- Erin D. Scully3,
- Yannick Pauchet4,
- Kelli Hoover5,
- Roy Kirsch4,
- Scott M. Geib6,
- Robert F. Mitchell7, 8,
- Robert M. Waterhouse9, 10,
- Seung-Joon Ahn4,
- Deanna Arsala11,
- Joshua B. Benoit12,
- Heath Blackmon13,
- Tiffany Bledsoe7,
- Julia H. Bowsher14,
- André Busch4,
- Bernarda Calla6,
- Hsu Chao15,
- Anna K. Childers16,
- Christopher Childers17,
- Dave J. Clarke1,
- Lorna Cohen11,
- Jeffery P. Demuth13,
- Huyen Dinh15,
- HarshaVardhan Doddapaneni15,
- Amanda Dolan18,
- Jian J. Duan19,
- Shannon Dugan15,
- Markus Friedrich20,
- Karl M. Glastad21,
- Michael A. D. Goodisman21,
- Stephanie Haddad1,
- Yi Han15,
- Daniel S. T. Hughes15,
- Panagiotis Ioannidis9,
- J. Spencer Johnston22,
- Jeffery W. Jones20,
- Leslie A. Kuhn23,
- David R. Lance24,
- Chien-Yueh Lee17, 25,
- Sandra L. Lee15,
- Han Lin17, 25,
- Jeremy A. Lynch11,
- Armin P. Moczek26,
- Shwetha C. Murali15,
- Donna M. Muzny15,
- David R. Nelson27,
- Subba R. Palli28,
- Kristen A. Panfilio29,
- Dan Pers11,
- Monica F. Poelchau17,
- Honghu Quan11,
- Jiaxin Qu15,
- Ann M. Ray30,
- Joseph P. Rinehart16,
- Hugh M. Robertson31,
- Richard Roehrdanz16,
- Andrew J. Rosendale12,
- Seunggwan Shin1,
- Christian Silva18,
- Alex S. Torson14,
- Iris M. Vargas Jentzsch29,
- John H. Werren18,
- Kim C. Worley15,
- George Yocum16,
- Evgeny M. Zdobnov9,
- Richard A. Gibbs15 and
- Stephen Richards15Email author
© The Author(s). 2016
Received: 4 August 2016
Accepted: 19 October 2016
Published: 11 November 2016
Relatively little is known about the genomic basis and evolution of wood-feeding in beetles. We undertook genome sequencing and annotation, gene expression assays, studies of plant cell wall degrading enzymes, and other functional and comparative studies of the Asian longhorned beetle, Anoplophora glabripennis, a globally significant invasive species capable of inflicting severe feeding damage on many important tree species. Complementary studies of genes encoding enzymes involved in digestion of woody plant tissues or detoxification of plant allelochemicals were undertaken with the genomes of 14 additional insects, including the newly sequenced emerald ash borer and bull-headed dung beetle.
The Asian longhorned beetle genome encodes a uniquely diverse arsenal of enzymes that can degrade the main polysaccharide networks in plant cell walls, detoxify plant allelochemicals, and otherwise facilitate feeding on woody plants. It has the metabolic plasticity needed to feed on diverse plant species, contributing to its highly invasive nature. Large expansions of chemosensory genes involved in the reception of pheromones and plant kairomones are consistent with the complexity of chemical cues it uses to find host plants and mates.
Amplification and functional divergence of genes associated with specialized feeding on plants, including genes originally obtained via horizontal gene transfer from fungi and bacteria, contributed to the addition, expansion, and enhancement of the metabolic repertoire of the Asian longhorned beetle, certain other phytophagous beetles, and to a lesser degree, other phytophagous insects. Our results thus begin to establish a genomic basis for the evolutionary success of beetles on plants.
Nitrogen, free amino acids, and protein are typically scarce in wood and access to sugars, minerals, and other key nutrients is severely impeded by lignified plant cell walls. Furthermore, woody plant tissues contain a diversity of allelochemicals that must be detoxified or sequestered when eaten . Successful feeding on woody plants therefore requires specialized metabolic adaptations. The genomes of A. glabripennis and certain other phytophagous beetles are known to contain genes encoding plant cell wall degrading enzymes (PCWDEs) [7–9]. PCWDEs degrade cellulose, hemicellulose, or pectin (the main polysaccharide networks in plant cell walls), liberating sugars, minerals, and other nutrients from woody plant tissues. Some cerambycid PCWDEs were originally obtained via horizontal gene transfer (HGT) from fungi or bacteria, and have subsequently diversified to form multi-gene families . This is in contrast to other wood feeding insects, e.g., termites and some ants and cockroaches, which have broadly similar metabolic capabilities conveyed by symbionts whose genomes contain many of the same families of genes . Additionally, lignin is degraded during passage through the A. glabripennis gut , suggesting a role for enzymes secreted into the gut by the beetle, its gut microbiota, or both parties. In vitro, PCWDEs and lignin-degrading enzymes encoded by the genomes of insects and their symbionts may be important in a wide range of biotechnological processes, including the production of biofuels and food [7, 8].
We investigated the genomic basis of specialized phytophagy on woody plants by A. glabripennis through genome and transcriptome sequencing and annotation, comparative genomic analyses, gene expression assays, and functional genomic studies. Complementary comparative analyses involving the A. glabripennis genome and 14 additional insect genomes, including two additional beetles whose genomes are studied here for the first time—the emerald ash borer (Agrilus planipennis, family Buprestidae) and the bull-headed dung beetle (Onthophagus taurus, family Scarabaeidae)—were undertaken to reconstruct broader patterns in the evolution of insect (especially beetle) genes encoding enzymes involved in the digestion of woody plant tissues or detoxification of plant allelochemicals.
Results and discussion
General genome features
Following insertion into eukaryotic genomes, bacterial HGTs will either degrade through mutational degradation or, occasionally, evolve into functional genes . In addition to glycoside hydrolase (GH) family genes (discussed in section titled Plant cell wall degradation), eight HGT candidates were found from bacteria to A. glabripennis using a DNA-based HGT pipeline  and junctions between the insertion and flanking sequences were confirmed in multiple libraries (Additional file 1: Table S7). The DNA based pipeline is effective at finding HGTs with DNA sequence similarity to their bacterial source even if they are not transcriptionally active [23–25]. Four candidates were from bacteria most closely related to Wolbachia, and two show high (95 %) sequence similarity to Wolbachia, suggesting relatively recent insertion. The other two show lower similarity (70–71 %) and contain indels and are, therefore, more likely to represent older insertions undergoing degradation. Other represented potential sources include, Calothrix, Clostridium, and Rickettsia. None of these HGT candidates showed significant expression in RNA-seq reads for adult males, females, or larvae, although this does not rule out expression in other stages or tissue-specific expression of these candidates below detection in whole organism RNA-seq. Recent insertions have similarly been detected in other arthropod genomes using the DNA-based pipeline [24, 25]. In contrast, the GH HGTs are more ancient insertions that have evolved into functional genes [26–30] (see results from in vitro functional characterization, discussed in section titled Plant cell wall degradation). No microbial scaffolds were found in the A. glabripennis assembly, likely because the tissues used for sequencing (Additional file 1) are not known to be associated with microbes.
A. glabripennis harbors similar numbers and kinds of genes involved in growth, development, and reproduction as Tribolium castaneum (and other insects; Additional file 1: Section VI). Some of these gene clusters (e.g., homeodomain transcription factors) correlate in scale with its genome size (~5× larger than T. castaneum) but also show A. glabripennis-specific paralogous expansion and gene dispersal. Key components of the genetic mechanisms underlying diapause in other insects were also found in the A. glabripennis genome. In contrast, A. glabripennis appears to possess an incomplete methylation machinery, including the maintenance methyltransferase DNMT1, but lacking the de novo methyltransferase DNMT3, which was lacking from both the genome assembly and the unassembled raw reads (Additional file 1: Section VI.10). While a similar situation is found in both T. castaneum and Drosophila melanogaster (common fruit fly, family Drosophilidae), many other insects, including other beetles such as Onthophagus taurus  and Nicrophorus vespilloides  (burying beetle, family Silphidae), have retained the complete machinery. A full description of the genes studied in the A. glabripennis genome can be found in Additional file 1.
Plant cell wall degradation
Plant cell wall degrading enzymes identified in the A. glabripennis genome assembly by manual annotation
GH5 subfamily 2
Reducing end-acting cellobiohydrolase
β-Glucosidase (myrosinase, cyanogenic β-glucosidase)
To determine substrate specificity and the contribution of enzymes encoded by GH family genes to the metabolism of plant cell wall polysaccharides, 15 of the 18 known A. glabripennis GH28 genes (putative polygalacturonases) were functionally characterized in vitro. Heterologous expression succeeded for all but GH28-4 (AGLA010098; Additional file 1: Figure S5). Most GH28 proteins were active against at least one homogalacturonan polymer in plate assays. A group of phylogenetically related proteins, GH28-1 (AGLA010095), -2 (AGLA010096), -3 (AGLA010097), and -5 (AGLA010099), all located in tandem on one genomic scaffold, showed no activity against homogalacturonan polymers (Additional file 1: Figures S5, S6b, S7). However, they did exhibit exopolygalacturonase activity, similar to a previously characterized GH28 from a near relative of A. glabripennis  (Additional file 1: Figure S6c). GH28-11 (AGLA002350), the only polygalacturonase expressed in both A. glabripennis larvae and adults , and GH28-17 (AGLA025090) both functioned as endopolygalacturonases; however, accumulation of galacturonic acid monomers was also observed for GH28-11, indicating that it could also function as an exopolygalacturonase (Additional file 1: Figure S6c). Overall, the repertoire of GH28 enzymes encoded by the A. glabripennis genome contains both endo- and exo-polygalacturonases and is able to act on substrates with varying degrees of methylation. These enzymes are highly complementary, allowing A. glabripennis to efficiently decompose pectinous homogalacturonan polymers present in the primary cell walls of living woody plant tissues.
Six GH5 genes, two GH45 genes, and one GH9 gene were also functionally characterized in vitro. GH5-1 (AGLA002353) functioned as an endo-β-1,4-xylanase (EC 18.104.22.168), GH5-2 (AGLA002352), GH5-5 (AGLA006972), GH45-1 (AGLA005419), and GH45-2 (AGLA005420) functioned as endo-β-1,4-glucanases (EC 22.214.171.124), and GH5-2 showed endo-β-1,4-xyloglucanase activity (EC 126.96.36.199) (Additional file 1: Figures S8b and S9). GH5-2 also hydrolyzed carboxymethylcellulose (CMC), indicating that enzymes encoded by this gene possess the ability to endohydrolyse the 1,4-β-D-glucosidic linkages in both CMC and xyloglucan and may function to degrade both cellulose and components of hemicellulose in vivo. GH5-3 (AGLA002354), GH5-4 (AGLA002351), GH5-6 (AGLA016376), and GH9 (AGLA010313) did not harbor any enzymatic activity against the substrates tested, indicating that they are not endo-acting enzymes. To investigate how GH5 enzymes degrade their substrates, the products were subsequently analyzed by thin layer chromatography (TLC) (see “Methods”; Additional file 1: Figure S8c), validating the roles of GH5-1 as a xylanase, GH5-2 as a dual-acting xyloglucanase/endoglucanase, and GH5-5 as an endoglucanase. Furthermore, although no zone of clearing was observed for GH5-6 in an agarose diffusion assay, accumulations of glucose and cellobiose were observed via TLC after incubation with CMC, suggesting that it functions as an exo-β-1,4-glucanase (Additional file 1: Figure S8c). None of these enzymes had the ability to degrade crystalline cellulose substrates. However, Geib et al.  observed activity against Avicel in enzyme extracts prepared from larval A. glabripennis guts. This suggests that (a) GH5 and GH45 cellulases act synergistically in vivo to degrade these substrates, (b) other A. glabripennis-encoded enzymes besides those characterized in this study possess the ability to degrade Avicel, or (c) that enzymes produced by the gut microbial community are responsible for the aforementioned previously observed activity. Notably, the cellulases encoded by numerous members of the A. glabripennis gut microbial community possess carbohydrate-binding domains, which could enhance the efficiency of these enzymes against crystalline substrates by allowing them to bind and degrade their substrates in a processive manner [30, 35]. Thus, the A. glabripennis genome encodes at least three families of cellulases and hemicellulases (subfamily 2 of GH5, GH9, and GH45) and one family of polygalacturonases (GH28) that provide it with an arsenal of enzymes capable of degrading the main polysaccharides of the cellulose and hemicellulose networks in both primary and secondary plant cell walls.
GH28, GH45, and subfamily 2 of GH5 were collectively detected only in the three phytophagous beetle genomes studied (A. glabripennis, A. planipennis and D. ponderosae) (Fig. 4; Additional file 1: Figure S18) and were lacking from the 12 other insect genomes. Specifically, GH28 was detected in A. glabripennis, A. planipennis, and D. ponderosae, GH45 was detected only in A. glabripennis and D. ponderosae (sister taxa in our phylogeny, spanning the basal split in the clade Phytophaga  (Fig. 2), and subfamily 2 of GH5 was detected exclusively in A. glabripennis. Subfamily 2 of GH5 genes have been found in at least one other cerambycid  and may be unique to superfamily Chrysomeloidea (leaf beetles, cerambycids, and their relatives). A. glabripennis, A. planipennis, and D. ponderosae are all specialized phytophages belonging to species-rich taxonomic groups of beetles that feed on the subcortical tissues of woody plants and interact with specialized suites of gut microbes. Interestingly, the genomes of the wood-feeding termites Macrotermes and Zootermopsis lack all three of the aforementioned gene families. However, these genes are present in the genomes of their gut symbionts. This is in contrast to the phytophagous beetles we studied, whose ancestors obtained these genes (in their genomes) via HGT from bacteria and fungi [8, 14] (Additional file 1: Figures S5 and S9). These genes subsequently diversified in beetle genomes to form multi-gene families . Notably, the GH28 family genes we annotated in A. planipennis were apparently acquired independently (via HGT from an ascomycete fungus donor) from those in A. glabripennis and D. ponderosae. Independently acquired GH28 genes are also known from phytophagous Hemiptera in the species-rich family Miridae .
GH1 family genes can encode enzymes having both digestive and non-digestive functions. Twenty-three A. glabripennis GH1 sequences had ~44 % identity to sequences annotated as myrosinases (MYR)  in the T. castaneum genome . One sequence closely matches known myrosinase active site motifs. For some insects, including flea beetles, myrosinases are known to synergize alarm or aggregation pheromones [39, 40]. Non-Brassicaceae, woody plant sources of glucosinolytes, which are the substrates detoxified by myrosinase, are present in the A. glabripennis native range . An additional possibility is that one or more of these A. glabripennis sequences is a cyanogenic β-glycosidase . Toxic cyanogenic glycosides are used by some plants (including known hosts of A. glabripennis) as a defense against insect-feeding, analogous to the myrosinase system. Interestingly, five A. glabripennis GH1 sequences are intermediate in similarity to known myrosinases and a known cyanogenic β-glycosidase (Additional file 1: Figure S16).
Microbes in the gut of A. glabripennis are known to have definitive roles in nutrient biosynthesis and nutrient recycling, helping the beetle to thrive under nutrient-poor conditions [35, 42, 43]. A. glabripennis microbes encode an arsenal of laccases, peroxidases, aldo-keto reductases, dyp-type peroxidases , and at least one lignin peroxidase, which is encoded by a fungal symbiont belonging to the F. solani species complex . Several of the aforementioned genes are actively expressed in the A. glabripennis larval midgut . While these enzymes have not been functionally characterized in vitro, they may facilitate lignin degradation in the A. glabripennis gut. The A. glabripennis genome itself may also encode genes that facilitate lignin degradation. A. glabripennis encodes eight genes with hemocyanin domains, three of which are significantly more highly expressed in larvae feeding in sugar maple, including the gene models AGLA002479 (2.1 log-fold upregulation), AGLA002478 (2.5 log-fold upregulation), and AGLA001233 (3.4 log-fold upregulation). All three genes were originally thought to function as storage hexamer proteins. However, the ability of at least one termite-derived hemocyanin highly expressed in salivary glands to oxidize model lignin compounds and other aromatic compounds in vitro , and the high expression levels of these three genes in multiple organisms that feed in wood , could signal that they work synergystically with gut microbes in A. glabripennis to facilitate oxidative degradation of prominent linkages in the lignin polymer and/or other biopolymers in vivo.
Detoxification of plant allelochemicals
To gain further insights into the genomic basis of the broad host range of A. glabripennis (>100 known host tree species) and its concomitant invasiveness, we studied gene families hypothesized to encode key enzymes involved in the detoxification of plant allelochemicals (Additional file 1: Tables S17–S26 and Figures S18–S22). Cytochrome P450s (CYP450; Additional file 1: Figure S21 and Tables S20 and S25) encode the most prevalent detoxification enzymes in insects and participate in many other important physiological processes. A total of 106 genes and 19 pseudogenes predicted to encode CYP450s were manually annotated in the A. glabripennis genome; 137 genes and 6 pseudogenes were detected by matches to InterPro domains, the third highest number in our comparative genomic study after the beetles T. castaneum and O. taurus. Examining the CYP450 sub-families showed that A. glabripennis had five times as many group II matches (18 genes; including CYP4 and CYP6) than the average across the other insect species studied. CYP6 enzymes metabolize a wide range of toxic compounds and are known to clear odorants in insect antennae . CYP4 enzymes are involved in cuticular hydrocarbon biosynthesis and have been implicated in insecticide resistance . Supporting their roles in detoxification, 25 CYP450 genes were induced in the guts of A. glabripennis larvae feeding in sugar maple, including many genes in A. glabripennis-specific clades (Additional file 1: Figure S10). Only two of the genes that were induced (CYP18A1, CYP314A1) occurred in orthologous pairs with T. castaneum genes. Therefore, while the many CYP450 ortholog pairs between T. castaneum and A. glabripennis presumably carry out functions conserved over millions of years of evolution, expansion of several CYP families and the evolution of A. glabripennis-specific CYP clades relative to T. castaneum suggests that these genes have evolved and diversified in A. glabripennis as a mechanism to overcome host plant defenses.
In addition, the A. glabripennis genome was found to contain more putative esterases than any of the other insect genomes studied (Additional file 1: Figure S20 and Tables S19 and S24). This is due mainly to a large expansion of type-B carboxylesterases (COesterases; IPR002018), most of which are paralogs. COesterases are important for the metabolism of xenobiotics and for degrading ester bonds linking lignin to hemicellulose in plant secondary cell walls. We identified 107 COesterases in the A. glabripennis genome (Additional file 1: Figure S14), more than double the average in the other species studied. Most COesterases occur in large clusters; only 28 (25 %) occur as singletons. Two large clades of COesterases, one containing 17 genes and the other 13 genes, were unique to A. glabripennis. A. glabripennis also had the most genes (eight total) matching the thioesterase domain (IPR001031). COesterases were among the most highly induced genes in A. glabripennis larvae feeding in sugar maple and most of the highly induced COesterases belonged to A. glabripennis-specific clades and formed tandem repeats in the genome, potentially signifying novel functions related to digestion of woody plant tissues or detoxification of plant allelochemicals.
Digestive proteinases may play key roles in scavenging nitrogen from plant cell wall proteins or midgut endosymbionts and may help phytophagous insects cope with proteinase inhibitors produced by plants . A. glabripennis-specific expansions of several proteinase OGs were observed in comparison to T. castaneum and D. ponderosae. The largest were OGs EOG8V724X and EOG8V19NQ, comprising tandem arrays of eight and seven trypsin genes, respectively. Both OGs contain genes predicted to encode secreted serine proteinases. Most proteinase genes were unique to each of the five beetle species studied, suggesting that their evolution occurred largely after speciation and may be correlated with exposure to different digestive enzyme inhibitors and with feeding on different diets. These gene families appear to be highly dynamic and may largely shape the digestive physiology of phytophagous insects.
A. glabripennis adults use a complex set of chemical and visual cues for host plant and mate finding. We compared the members of four gene families involved in chemoperception (olfaction and gustation) and vision in A. glabripennis with those from T. castaneum and D. melanogaster. We manually annotated 52 odorant binding protein (OBP) genes in the A. glabripennis genome (Additional file 1: Figure S23). Most OBPs comprise a large expansion of the minus-C subfamily, and the remaining genes were placed singly or in small radiations that exhibit the classic 6-cysteine motif. One OBP (AglaOBP51) was identified as a member of the plus-C group, the same as in T. castaneum and D. ponderosae , suggesting that the tendency toward minus-C OBPs originated at least with the beetle infraorder Cucujiformia (~190 Ma) . A. glabripennis has 131 odorant receptor (OR) genes in addition to the highly conserved OR co-receptor Orco (Additional file 1: Figure S24). These include representatives of all seven subfamilies of beetle ORs except group 6 and follow the pattern of frequent paralogous radiations typical of insect chemoreceptors. Two new lineages of ORs were identified in A. glabripennis and placed as outgroups to OR groups 4, 5, and 6 in T. castaneum (Or106-115/126-132 and Or101-103). The function of beetle ORs remains mostly unknown, and receptors have only been characterized from Megacyllene caryae (hickory borer, family Cerambycidae; McarOr3). AglaOr29 is notably sister to McarOr3, which is sensitive to 2-methylbutan-1-ol, a pheromone component of Megacyllene .
A. glabripennis has an extensive suite of 234 gustatory receptors (GRs), including three conserved candidate CO2 receptors (Gr1–3), ten candidate sugar receptors (Gr4–13), and three candidate fructose receptors related to DmGr43a (Gr14–16). The remaining 127 GRs encode 218 receptors through alternative splicing and presumably belong to the general category of candidate bitter taste receptors, although some likely are also involved in contact pheromone perception , a component of A. glabripennis mate-finding behavior . A. glabripennis has 72 ionotropic receptors (IRs), including orthologs of the conserved co-receptors IR8a and 25a and of IR21a, 40a, 41a, 68a, 76b, 93a, and 100a. The IR75 lineage consists of eight genes compared with six in T. castaneum and seven in D. melanogaster. These are all candidate ORs, while the candidate GRs, represented by the DmIr20a clade of 40 genes , consist of 55 genes, compared to 53 in T. castaneum, although these two beetles exhibit differential species-specific expansion of gene lineages within this large grouping. Like T. castaneum [15, 57], A. glabripennis has large OR and GR repertoires compared with D. melanogaster, and indeed most other insects except ants, but their OBP and IR repertoires are more comparable with that of D. melanogaster and similar to many other insects (Additional file 1: Table S27). The optical sensitivity of A. glabripennis appears to be similar to that of T. castaneum . A. glabripennis has a single long-wavelength-sensitive opsin and a single UV-sensitive opsin. A. glabripennis differs from T. castaneum, however, in having the Rh7 opsin, whose function is unknown, and in lacking the c-opsin found in most other insects and other arthropods, which is presumed to have a non-visual function .
A. glabripennis possesses a remarkably robust enzymatic repertoire capable of digesting most of the polysaccharides it encounters while feeding on woody host plants (cellulose, xyloglucan, xylan, and pectin). Furthermore, diverse suites of detoxification genes and several classes of digestive proteinases provide A. glabripennis with the metabolic plasticity needed to overcome the challenges of feeding on different host trees, each with a distinct profile of defensive compounds. Many of the paralogs in gene families encoding enzymes typically involved in plant cell wall degradation (PCWDEs) and detoxification occur in large clusters in the A. glabripennis genome and appear to have diversified by tandem gene duplication. Large expansions of genes encoding CYP450s, UGTs, COesterases (these three together are sometimes called the defensome; e.g., ) and GH1s in the A. glabripennis genome are particularly notable, as they are among the largest such repertoires of detoxification genes known in insects. Genes encoding PCWDEs are also uniquely expanded in number in the A. glabripennis genome. The A. glabripennis genome encodes genes from a remarkable three families of putative cellulases (GH5 subfamily 2, GH9, and GH45), and one of these, GH5 subfamily 2, evolved in such a way that it provides the beetle with an arsenal of enzymes possessing the ability to degrade the main polysaccharides of the cellulose and hemicellulose (xylan and xyloglucan) networks in both primary and secondary plant cell walls. A. glabripennis also has the ability to degrade lignin, either through the activities of its gut microbial fauna and/or by way of enzymes encoded in its genome. Our results are notable in including not only an enumeration of genes potentially involved in plant cell wall degradation and detoxification (thus facilitating specialized phytophagy on woody plants and a wide host range), but also results from experimental assessments of gene expression and enzyme activities.
Acquisition of new genes (here, GH5, GH28, and GH45 family genes) via HGT from bacteria and fungi followed by gene copy number amplification and functional divergence contributed to the addition, expansion, and enhancement of the metabolic repertoire of A. glabripennis, certain other beetles, and, to a lesser degree, other phytophagous insects. Our results thus further establish a genomic basis for the invasiveness and broad host plant range of A. glabripennis and reveal genomic innovations potentially underlying the evolutionary success of insects—especially beetles—on plants.
Genome size and DNA and RNA for sequencing
The genome size of five male and five female adult A. glabripennis collected from the former Chicago, IL, USA infestation were estimated via flow cytometry. The A. glabripennis specimens sequenced for this project were obtained from a USDA-APHIS colony stocked with the descendants of beetles collected from current and former infestations in IL, NY, and MA, except when noted otherwise in the supplement (Additional file 1: Table S1). The A. glabripennis genome was sequenced from DNA that was extracted from a single late instar female larva (G Biosciences, Omniprep kit), whose sex was determined after sequencing (Additional file 1: Figure S3).
Genome sequencing and assembly
An enhanced Illumina-ALLPATHS-LG  sequencing and assembly strategy was employed. We sequenced four libraries of nominal insert sizes 180 bp, 500 bp, 3 kb, and 8 kb at genome coverages of 59.7×, 45.8×, 58.7×, and 20.5×, respectively. Sequencing was performed on Illumina HiSeq2000s generating 100-bp paired-end reads. Reads were assembled using ALLPATHS-LG (v35218) and further scaffolded and gap-filled using in-house tools Atlas-Link (v.1.0) and Atlas gap-fill (v.2.2) (https://www.hgsc.bcm.edu/software/). Data for the A. glabripennis genome have been deposited in the GenBank/EMBL/DDBJ Bioproject database under the accession code PRJNA163973 (Additional file 1: Table S3). Raw genomic sequence data have been deposited in the GenBank/EMBL/DDBJ Sequence Read Archive under the accession codes SRX326764, SRX326768, SRX326767, SRX326766, and SRX326765. The genome assembly has been deposited to GenBank under the accession GCA_000390285.1. RNA-seq datasets used in gene prediction have been deposited to the GenBank/EMBL/DDBJ sequence read archive under the accession codes SRX873913 and SRX873912.
The A. glabripennis genome assembly was subjected to automatic gene annotation using a MAKER 2.0 [18, 24, 62] annotation pipeline tuned for arthropods. Both protein and RNA-seq evidence from extant arthropod gene sets were used to guide gene models. The genome assembly was first subjected to de novo repeat prediction and Core Eukaryotic Genes Mapping Approach (CEGMA) analysis  to generate gene models for initial training of the ab initio gene predictors. Three rounds of training of the Augustus  and SNAP  gene predictors within MAKER were used to bootstrap to a high quality training set. RNA-seq data from A. glabripennis adult males and females was used to identify exon–intron boundaries. Finally, the pipeline used a nine-way homology prediction with human, D. melanogaster, and Caenorhabditis elegans, and InterPro Scan5 to allocate gene names. The automated gene set is available from the BCM-HGSC website (https://www.hgsc.bcm.edu/asian-long-horned-beetle-genome-project) and at the National Agricultural Library (https://i5k.nal.usda.gov).
The A. glabripennis genome was curated to improve the structural and functional annotations of genes and gene families of interest using the Web Apollo manual curation tool  (Additional file 1: Table S4; Additional file 2: Tables S5 and S6). Web Apollo is an interactive, web-based manual curation tool that visualizes user-generated annotation changes in real time, allowing remote collaboration on annotations. The A. glabripennis genome coordinator (D. McKenna, University of Memphis) organized a group of experts to manually curate genes or gene families of interest in Web Apollo. Web Apollo (https://apollo.nal.usda.gov/anogla/jbrowse/) tracked all evidence used for the MAKER gene predictions, as well as an additional RNA-seq dataset that was not used in the generation of the MAKER gene predictions. The manually curated models were inspected for quality, including overlapping models, internal stop codons within the coding sequence, gff3 formatting errors, and mixed transcript types within gene models. The quality-corrected models were then merged with the MAKER-predicted gene set to generate an official gene set (OGS), followed by post-processing to ensure curation information was transferred adequately. A full list of conditions for mRNA, gene, exon, and coding sequence is provided in Additional file 1: Table S5. All functional information was included in the OGS. Information on the A. glabripennis genome project is collated at the i5k Workspace  (https://i5k.nal.usda.gov/Anoplophora_glabripennis), and the genome, transcript, and protein sets can be searched via BLAST and browsed via the JBrowse genome browser  (https://apollo.nal.usda.gov/anogla/jbrowse). All manually curated genes and transcripts and their curation actions are provided in Additional file 2: Table S6. Additional details on annotation methods are provided in the Additional file 1.
Assessing orthology and the quality of genome assembly and annotation
Orthology data from OrthoDB v8  with a total of 87 arthropod species were analyzed to identify orthology and homology assignments of A. glabripennis genes with those of other beetles and representative species from six other insect orders. The gene sets of A. planipennis and O. taurus (unpublished data, manuscript in preparation; Fig. 2) were mapped to OrthoDB v8 orthologous groups (OGs) to include them in the analysis. The selected species include several that feed on plants and were partitioned into three species sets: five Coleoptera, five Lepidoptera/Diptera, and five outgroup insects. Arthropod OGs were queried with custom Perl scripts to identify OGs with genes from all three species sets (across 15 species), just two sets (across ten species), or restricted to a single set (across five species). To be considered shared, OGs were required to contain genes from at least two species in each set. For those shared among all three sets (a total of 7376 OGs), the numbers of single-copy and multi-copy orthologs were summed across all OGs for each species. Lineage-restricted genes without orthologs were assessed for significant homology (e-value <1e − 05) to other arthropod genes from OrthoDB or for significant homology (e-value <1e − 05) to genes from their own genomes (self-only homology). The completeness of the A. glabripennis genome assembly and annotated offical gene set (OGS) were assessed using BUSCOs . We compared the results from A. glabripennis to those from 14 other insect genomes (Fig. 2b; Additional file 1: Figure S1). We used the Arthropoda gene set, which consists of 2675 single-copy genes that are present in at least 90 % of Arthropoda.
Identification of bacterial to eukaryote HGTs
HGTs were identified as described in Wheeler et al. . Briefly, we used BLASTN to compare genomic scaffolds against a bacterial database containing 1097 complete bacterial genome sequences downloaded from the National Center for Biotechnology Information (NCBI). Regions with significant bacterial identity (E value <1e − 5) were then compared to a second database containing representative animal genomes (see Wheeler et al.  for a list of animal species) obtaining a corresponding “animal” BLASTN E value score. If the animal E value score was less than the bacterial E value score the sequence was excluded as a slowly evolving highly conserved gene. Candidates were then further annotated manually for flanking eukaryotic genes and junctions between eukaryotic and bacterial sequences in the libraries. For glycoside hydrolases, the same methods were used, but we additionally simply BLASTed the genome using sequences of known, characterized PCWDEs found in phytophagous beetles [8–10], including Apriona japonica , a close relative of A. glabripennis.
Differential expression analysis of A. glabripennis larvae feeding on sugar maple versus artificial diet
Five pairs of adult male and female A. glabripennis were allowed to maturation feed on fresh twigs collected from Norway maples (Acer platanoides, family Aceraceae) for two weeks. After this period, the beetles were allowed to mate and oviposit into potted sugar maple trees (Acer saccharum) maintained in a USDA-approved quarantine greenhouse for two weeks. The trees were harvested approximately 60 days after the eggs hatched and four third-instar larvae were collected. Four third-instar larvae feeding on an artificial diet  were also harvested. Larvae were surface sterilized, dissected, and their midguts were removed and frozen in liquid nitrogen. RNA was isolated, and ribosomal RNA was depleted from the sample using a Ribominus Eukaryotic Kit for RNA-seq (Life Technologies). The enriched mRNA was further poly(A) purified and multiplexed Illumina libraries were constructed using the TruSeq RNA Sample Prep kit (Illumina, San Diego, CA, USA). Samples were pooled and sequenced on a single Illumina HiSeq lane at the University of Delaware Biotechnology Institute (Newark, DE, USA) to generate approximately 13 million 101-nucleotide paired-end reads per sample. Forward reads were trimmed and quality filtered using ea-utils (https://expressionanalysis.github.io/ea-utils/) and high quality reads of at least 75 nucleotides in length were mapped to the A. glabripennis reference genome assembly using TopHat . Read counts that mapped to each locus (version v0.5.3 annotations) were summed using HTSeq ; reads that spanned multiple features were summed using the union mode and reads that did not map uniquely to a single region in the genome were discarded. Differential expression analysis was performed using edgeR . Features with less than ten mapped reads were removed from the analysis, read counts were normalized by quantile normalization, and variances were estimated using tagwise dispersions. Statistical analysis was performed using Fisher’s exact tests; features were flagged as differentially expressed if they had a log fold change greater than 1.0 and an adjusted p value of <0.05. Experiment-wise false discovery rate (FDR) was estimated at 0.05. The raw Illumina reads used for the differential expression analysis have been deposited into NCBI’s Sequence Read Archive (SRA) and are associated with Bioproject PRJNA279780. The read counts used to compute differential expression have been deposited in Gene Expression Omnibus (GEO) under the accession GSE68149.
In vitro functional characterization of plant cell wall degrading enzymes
A. glabripennis larval samples were obtained from D. Lance (USDA-APHIS-PPQ). Larvae were chilled on ice and cut open; midguts from 1.5-month-old, 4-month-old, and 8-month-old larvae were collected and stored in an excess of RNA Later solution (Ambion) prior to shipping. RNA was subsequently isolated using the innuPREP RNA Mini Kit (Analytik Jena) according to the manufacturer’s protocol. Genomic DNA contamination was removed by DNAse treatment (TURBO DNAse, Ambion) for 30 min at 37 °C. Midgut RNA was further purified using the RNeasy MinElute Clean up Kit (Qiagen) following the manufacturer’s protocol and eluted in 20 μl of RNA storage solution (Ambion). Integrity and quality of the RNA samples were determined using the RNA 6000 Nano LabChip kit (Agilent Technologies) on an Agilent 2100 Bioanalyzer (Agilent Technologies) according to the manufacturer’s instructions.
Open reading frames encoding putative PCWDEs were amplified by PCR using gene-specific primers. The forward primer was designed to introduce a 5′ Kozak sequence, and the reverse primer was designed to omit the stop codon. Equal amounts of total RNA prepared from midguts either of 1.5-month-old or 4-month-old or 8-month-old larvae were pooled, and 1 μg total RNA from this pool was used to generate first-strand cDNAs using the SMARTer RACE cDNA Amplification Kit (BD Clontech) following the manufacturer’s instructions. These cDNAs were subsequently used as templates for PCR amplifications. PCR products were cloned into the pIB/V5-His TOPO/TA (Invitrogen) vector, in frame with a V5-(His)6 epitope at the carboxyl terminus. Constructs were transfected into insect Sf9 cells, which were grown to confluence, and expression of the recombinant proteins was validated as described previously . Diffusion assays were performed using 1 % agarose Petri dishes in McIlvaine buffer (pH 5.0) containing one of the following substrates: 0.1 % carboxymethylcellulose (CMC, Sigma-Aldrich); 0.1 % beechwood xylan (Sigma-Aldrich); 0.1 % xyloglucan from tamarind seeds (Megazyme); 0.1 % pectin from citrus peels (Sigma-Aldrich); 0.1 % demethylated polygalacturonic acid (Megazyme). Enzyme activity was detected using a 0.1 % Congo Red solution as described previously .
TLC analysis of hydrolysis reaction products was also performed. The culture medium of transiently transfected cells was first dialyzed against distilled water at 4 °C for 48 h, using Slide-A-Lyzer Dialysis Cassettes with a 10-kDa cutoff, before being desalted with Zeba Desalt Spin Columns with a 7-kDa cutoff (both Thermo Scientific), according to the manufacturer’s instructions. Enzyme assays (20 μl) were set up using 14 μl of dialyzed and desalted crude enzyme extracts mixed with 4 μl of a 1 % substrate in solution in a 20 mM McIlvaine buffer (pH 5.0). For GH5-1 to -6, the following substrates were tested: carboxymethyl cellulose (CMC), avicel (suspension), beechwood xylan, and xyloglucan. For GH28s, the following substrates were tested: demethylated polygalacturonic acid and pectin from citrus peels. The activity of GH28s on 10 μg/μl aqueous solution of tri- and di-galacturonic acid was also tested. Enzyme assays were incubated and plates developed as described previously .
Amino acid alignments were carried out using MUSCLE version 3.7 on the Phylogeny.fr web platform (http://www.phylogeny.fr)  and were inspected and corrected manually when needed. Bayesian analyses were carried out in MrBayes 3.1.2 . Two runs were conducted for the dataset showing agreement in topology and likelihood scores. To obtain support from a second independent method, maximum likelihood analyses were also performed using MEGA5 . The robustness of each analysis was tested using 1000 bootstrap replicates.
Comparative genomics of phytophagy and detoxification across Insecta
Gene families and subfamilies associated with phytophagy (particularly xylophagy) and polyphagy or detoxification were identified by searching for matches to relevant InterPro domains in the complete gene sets from the genomes of 15 exemplar insect species. These included five beetles (A. glabripennis, D. ponderosae, T. castaneum, A. planipennis (unpublished), and O. taurus (unpublished)); five basal insects (Zootermopsis nevadensis (dampwood termite, family Termopsidae), Pediculus humanus (human louse, family Pediculidae), A. pisum, Apis mellifera (honey bee, family Apidae), and Nasonia vitripennis (jewel wasp, family Pteromalidae)); two lepidopterans (Plutella xylostella (diamondback moth, family Plutellidae) and Danaus plexippus (monarch butterfly, family Nymphalidae)); and three dipterans (Mayetiola destructor (Hessian fly, family Cecidomyiidae), D. melanogaster, and Anopheles gambiae (African malaria mosquito, family Culicidae)). Protein domains were annotated with InterProScan5  using the following domain libraries: PfamA-27.0, PrositeProfiles-20.97, SMART-6.2, SuperFamily-1.75, and PRINTS-42.0. The gene families examined included glycoside hydrolases, peptidases, esterases, cytochrome P450s, and UDP-glucosyltransferases.
The classifications based on InterPro domain counts were used only for those cases where the maximum gene count in a given species was greater than 5 (i.e., at least one species had a potential expansion of more than five genes). The orthology status of each of these identified genes was assessed using OrthoDB v8  to determine if the gene was found as a single-copy ortholog, or with co-orthologs, or whether it showed homology to the domain but was not classified in any orthologous group. The results of the counts of each relevant domain type and the orthology status for the identified genes are given in Additional file 1: Tables S17–S26. Domains were selected for plotting from the complete list to avoid redundant domains (e.g., subfamilies rather than families and just one of N/C-terminal domains). For each gene family, the bar charts were plotted with largest subfamily at the bottom and smallest at the top, showing the counts for each subfamily per species (Additional file 1: Figures S18–S22). The orthology status of genes in the subfamily bar charts (i.e., those plotted and where at least one species has more than five genes) show the totals in each species partitioned into homologs and single-copy and multi-copy orthologs (Additional file 1: Tables S19–S23).
We thank S. Raschka (MI State University), and K. Morris, V. Lopez, S. Gula, and B. Walters (Xavier University), M. Munoz-Torres (Lawrence-Berkeley National Lab), B. Wurlitzer and D. Schnabelrauch (Max Plank Institute for Chemical Ecology), K. Kuhn and E. Aparicio (USDA ARS BIIR), and J. Johnson (ND State University) for their assistance with this research, and D. Hibbett (Clarke University) for comments on an early draft of the manuscript.
Funding for genome sequencing, assembly and automated annotation was provided by NHGRI grant U54 HG003273 to RAG. The i5k pilot project (https://www.hgsc.bcm.edu/arthropods) assisted in sequencing of the A. glabripennis, A. planipennis, and O. taurus genomes. We acknowledge funding from the University of Memphis FedEx Institute, US NSF grant DEB1355169 and USDA-APHIS cooperative agreement 15-8130-0547-CA to DDM, USDA NIFA grant 2015-67013-23287 to KH and ES, NSF grant DEB1257053 to JHW, NSF grants IOS1120209 and IOS1256689 to APM, University of Cincinnati Faculty Development Research grant to JBB, Marie Curie International Outgoing Fellowship PIOF-GA-2011-303312 to RMW, Swiss NSF awards 31003A-125350 and 31003A-143936 to EMZ, Max-Planck-Gesellschaft to YP, RK and AB, German Research Foundation (DFG) grants PA 2044/1-1 and SFB 680 to KAP, and NIH postdoctoral training grant 5 K12 GM000708-15 to RFM.
Availability of data and materials
All sequence data are publically available at the NCBI, bioproject number PRJNA167479. Additional file 1: Table S3 gives specific details of accession numbers for specific raw and assembled DNA and RNA sequences. In addition, gene models and a browser are available at the National Agricultural Library (https://i5k.nal.usda.gov/Anoplophora_glabripennis).
DDM and SR conceived, managed, and coordinated the project. DL provided specimens for sequencing. DDM performed DNA and RNA extractions. SR, HuD, YH, HaD, DMM, and RAG managed library preparations and sequencing. SR, SLL, and HC constructed libraries and performed sequencing. SCM, JQ, DSTH, SR, and KCW performed the genome assembly and automated gene prediction. DDM, MFP, CC, CL, and HL developed and implemented WebApollo manual curation. RMW, EMZ, and PI performed orthology and phylogenomic analyses. DDM, SA, DA, AB, JBB, TB, JB, BC, LC, MAD, MF, KMG, MADG, SH, IMVJ, JSJ, JWJ, LK, RK, JAL, RM, DRN, SRP, KAP, DP, SP, YP, HQ, AR, JR, HR, RLR, AJR, EDS, AT, and GY participated in manual curation and contributed to subprojects and/or the supporting information. JSJ analyzed genome size. HB and JPD studied genome organization and chromosome synteny. KMG and MADG conducted analyses of DNA methylation. AD, CS, and JW studied bacterial horizontal gene transfers. RK, AB, and YP performed in vitro functional characterization of PCWDEs. EDS, KH, and SMG studied gene expression. LK, AMR, and EDS studied myrosinase and cyanogenic β-glycosidase-like sequences. RMW, JJD, SMG, DDM, AM, and EDS contributed to comparative genomic analyses. DDM, EDS, KH, LAK, JBB, SMG, YP, and SR wrote the manuscript. DDM, SR, DJC, and SS organized the supporting information. All authors approved the final manuscript.
The authors declare that they have no competing interests.
Ethics approval and consent to participate
Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.
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