Abstract
The orchid genus Dipodium R.Br. (Epidendroideae) comprises leafy autotrophic and leafless mycoheterotrophic species, with the latter confined to sect. Dipodium. This study examined plastome degeneration in Dipodium in a phylogenomic and temporal context. Whole plastomes were reconstructed and annotated for 24 Dipodium samples representing 14 species and two putatively new species, encompassing over 80% of species diversity in sect. Dipodium. Phylogenomic analysis based on 68 plastid loci including a broad outgroup sampling across Orchidaceae found that sect. Leopardanthus is the sister lineage to sect. Dipodium. Dipodium ensifolium, the only leafy autotrophic species in sect. Dipodium, was found to be a sister to all leafless, mycoheterotrophic species, supporting a single evolutionary origin of mycoheterotrophy in the genus. Divergence-time estimations found that Dipodium arose ca. 33.3 Ma near the lower boundary of the Oligocene and that crown diversification commenced in the late Miocene, ca. 11.3 Ma. Mycoheterotrophy in the genus was estimated to have evolved in the late Miocene, ca. 7.3 Ma, in sect. Dipodium. The comparative assessment of plastome structure and gene degradation in Dipodium revealed that plastid ndh genes were pseudogenised or physically lost in all Dipodium species, including in leafy autotrophic species of both Dipodium sections. Levels of plastid ndh gene degradation were found to vary among species as well as within species, providing evidence of relaxed selection for retention of the NADH dehydrogenase complex within the genus. Dipodium exhibits an early stage of plastid genome degradation, as all species were found to have retained a full set of functional photosynthesis-related genes and housekeeping genes. This study provides important insights into plastid genome degradation along the transition from autotrophy to mycoheterotrophy in a phylogenomic and temporal context.
Keywords: Dipodium, divergence-time estimation, gene degradation, mycoheterotrophy, phylogenetics, plastome
1. Introduction
Heterotrophic plants—plants that rely on other organisms for energy and nutrients—are remarkable survivors, exhibiting often curious morphological, physical, or genomic modifications, reflecting evolutionary relaxed selective pressure on photosynthetic function (Graham et al., 2017; Barrett et al., 2019). Advances in next-generation sequencing and bioinformatic pipelines have vastly accelerated the characterisation of plastid genomes (plastomes), including heterotrophic plants, providing new insights into plastome evolution. Plastomes of heterotrophic plants often exhibit greatly altered structure and gene content due to photosynthesis-related genes that are no longer required (Delannoy et al., 2011; Barrett et al., 2014; Lam et al., 2015; Braukmann et al., 2017; Graham et al., 2017; Barrett et al., 2018; Wicke and Naumann, 2018; Barrett et al., 2019; Qu et al., 2019; Klimpert et al., 2022; Peng et al., 2022; Wen et al., 2022). Hence, heterotrophic plants offer excellent opportunities to gain insight into plastome evolution under relaxed selection.
Early non-phylogenomic studies on plastome evolution in heterotrophic plants allowed the discovery of large-scale plastome evolutionary patterns and stimulated research into fine-scale, phylogenetic comparative approaches (e.g., Delannoy et al., 2011; Logacheva et al., 2011; Roma et al., 2018). Thus far, most phylogenetic comparative studies included plastomes of taxa scattered across families, tribes, or genera (e.g., Kim et al., 2015; Feng et al., 2016; Niu et al., 2017; Lallemand et al., 2019; Kim et al., 2020; Li et al., 2020; Tu et al., 2021; Kim et al., 2023). Nevertheless, phylogenetic, comparative approaches at the infrageneric level are still scarce (e.g., Barrett et al., 2018, 2019).
Orchidaceae, one of the two largest flowering plant families, has undergone a greater number of independent transitions from autotrophy to heterotrophy than any other land plant lineage (Merckx, 2013; Christenhusz and Byng, 2016; Jacquemyn and Merckx, 2019). The family comprises several heterotrophic orchid lineages that rely to some extent on mycorrhizal fungi for carbon and other nutrients, i.e., initial, partial, or full mycoheterotrophy (Merckx, 2013).
So far, most examined mycoheterotrophic orchid plastomes exhibited degradation patterns similar to those found in heterotrophic plastomes of other plants. These include a reduction in genome size, a decrease in guanine–cytosine (GC) content, rearrangements, pseudogenisations, and gene losses (e.g., Delannoy et al., 2011; Barrett et al., 2018, 2019; Lallemand et al., 2019; Wen et al., 2022). Moreover, whole plastome sequencing has revealed patterns of plastid gene degradation for various heterotrophic plastomes that led to the development of conceptual models to predict the evolutionary transition from autotrophy to heterotrophy of the plastid organelle (e.g., Graham et al., 2017; Barrett et al., 2019). Several studies in mycoheterotrophic orchid lineages found support for these models that predict a progression from losses of the chloroplast ndh genes to genes encoding complexes that are directly involved in photosynthesis (e.g., psa and psb) to more general “housekeeping” genes (e.g., accD and matK) (Barrett et al., 2018; Wicke and Naumann, 2018; Barrett et al., 2019; Kim et al., 2020, 2023).
Interestingly, degraded ndh genes were also found in some autotrophic orchids (e.g., Kim et al., 2015; Kim and Chase, 2017; Niu et al., 2017; Lallemand et al., 2019; Kim et al., 2023). This appears curious, as the ndh genes encode proteins of the NADH dehydrogenase complex (NDH complex), which is assumed to play a role in cyclic electron flow and thus fine-tunes photosynthesis (Yamori et al., 2015; Peltier et al., 2016). The degradation of ndh genes is hypothesised to have led to additional structural changes in the plastome (Kim et al., 2015). In particular, ndhF gene loss was correlated with shifts in the position of the junction of the inverted repeat/small single copy (IR/SSC) region in Orchidaceae and other plants (Kim et al., 2015; Niu et al., 2017; Dong et al., 2018; Roma et al., 2018; Thode and Lohmann, 2019; Könyves et al., 2021; Li et al., 2021). However, within Orchidaceae, degradation of ndh genes was found to vary even among closely related species (e.g., Kim et al., 2015; Feng et al., 2016; Kim and Chase, 2017; Barrett et al., 2018, 2019), which suggests the genes for the NDH complex may be under relaxed selective pressure in several orchid lineages (Kim and Chase, 2017). Moreover, previous studies found that ndh degradation patterns vary considerably and have been independently degraded among orchids (Kim et al., 2015; Kim and Chase, 2017; Niu et al., 2017; Lallemand et al., 2019).
The orchid genus Dipodium R.Br. (Cymbidieae) contains both autotrophic and mycoheterotrophic species and thus represents a suitable model system in which to address hypotheses of plastome evolution. The genus comprises 39 species and is divided into two sections, Dipodium and Leopardanthus (Blume) O. Kuntze, based on morphological and geographical evidence (O’Byrne, 2017; Jones, 2021). Sect. Leopardanthus (26 species) is distributed in the floristic regions of Malesia and Australasia (O’Byrne, 2017). All species of sect. Leopardanthus are green leafy plants and non-uniform in habit (O’Byrne, 2017). Section Dipodium (13 species) occurs predominantly in Australasia, with nearly all species being endemic to Australia. One species occurs in New Guinea (Dipodium elatum J.J. Sm.), one species extends into the Pacific region [Dipodium squamatum (G.Forst.) Sm. (New Caledonia and Vanuatu)], and one occurs in Malesia (Dipodium gracile Schltr. (Sulawesi) (Schlechter, 1911; O’Byrne, 2017; POWO, 2023; WFO, 2023). In contrast to sect. Leopardanthus, most species of sect. Dipodium are non-climbing terrestrials, forming subterranean rhizomes and erect flowering stems with highly reduced, non-photosynthetic leaves (i.e., scales) ( Figure 1B ). Leafless species within sect. Dipodium are generally assumed to be mycoheterotrophic (O’Byrne, 2014). However, the extent to which non-leafy species in Dipodium are mycoheterotrophic is unclear. Whereas they have been assumed to be fully heterotrophic in the past, recent research in Dipodium roseum points to partial instead of full mycoheterotrophism (McLay et al., 2023). Among the Australian species of sect. Dipodium, Dipodium ensifolium F. Muell. stands out as a leafy terrestrial ( Figure 1A ).
The aims of this study were as follows:
sequence and assemble plastid genomes for species of Dipodium to elucidate patterns of plastid genome modification (e.g., rearrangement, structural variation, pseudogenisation, and gene loss) across autotrophs and mycoheterotrophs within the genus and examine gene degradation in the context of current models of plastome degradation in heterotrophic plants,
infer phylogenomic relationships within section Dipodium and among closely related autotrophic relatives (i.e., Dipodium section Leopardanthus), and
estimate divergence times of Dipodium to assess the origin of mycoheterotrophy within the genus and elucidate over which evolutionary timeframe plastid gene degradation and losses have taken place within Dipodium.
2. Material and methods
2.1. Plant material
For this study, we sampled all known Australian species of section Dipodium and one representative of section Leopardanthus ( Table 1 ). Based on previous molecular systematic studies (Serna-Sánchez et al., 2021; Pérez-Escobar et al., 2023; Zhang et al., 2023), an extended outgroup from closely related orchid genera within subtribe Eulophiinae (Eulophia R.Br., Geodorum Andrews) and subtribe Cymbidiinae (Cymbidium Sw., Acriopsis Reinw. ex. Blume) was sampled ( Table 1 ). Specimens studied were from different regions within Australia, with the exception of one specimen from Papua New Guinea (Dipodium pandanum 2) ( Table 1 ).
Table 1.
Species | DNA extract no. | Voucher details | Provenance |
---|---|---|---|
Dipodium aff. roseum 1 | HTCG 0828 | C. Bower ORG7817 (CANB 906470.1) | AU: NSW; Central Tablelands; Mullions Range State Forest |
Dipodium aff. roseum 2 | HTCG 0830 | C. Bower ORG7818 WP 6 (CANB 906471.1) | AU: NSW; Central Tablelands; Mount Canobolas State Conservation Area |
Dipodium aff. roseum 3 | HTCG 0831 | C. Bower ORG7818 WP 7 (CANB 906471.1) | AU: NSW; Central Tablelands; Mount Canobolas State Conservation Area |
Dipodium aff. roseum 4 | HTCG 0832 | C. Bower ORG7818 WP 9,10,11 (CANB 906471.1) | AU: NSW; Central Tablelands; Mount Canobolas State Conservation Area |
Dipodium aff. stenocheilum | HTCG 1691 | D.L. Jones 8968 (CBG 9220253.1) | AU: QLD; Cook; Mount Elliot |
Dipodium ammolithum | HTCG 1372 | M.D. Barrett 4910A (PERTH) |
AU: WA; North Kimberley, Theda Station |
Dipodium atropurpureum 1 | HTCG 0760 | W.M. Dowling DC 1717 (CANB 924629.1) | AU: NSW; Northern Tablelands; Barrington Tops State Forest |
Dipodium atropurpureum 2 | HTCG 1679 | M.A. Clements 4426 (CBG 8605570.1) | AU: NSW; Northern Tablelands; New England Highway to Armidale |
Dipodium basalticum | HTCG 1693 | D.E. Murfet 4837 (CANB 662327.1) | AU: NT; Darwin and Gulf; near Nhulunbuy |
Dipodium campanulatum 1 | HTCG 1680 | K. Alcock DLJ5622 (CBG 9004646.2) | AU: SA; South-east; Naracoorte |
Dipodium campanulatum 2 | HTCG 1681 | D.E. Murfet 1930b (CANB 677107.2) | AU: SA; South-east; Penola Conservation Park |
Dipodium elegantulum | HTCG 1682 | L. Lawler 8 (CBG 8605836.1) | AU: QLD; Cook; near Mareeba |
Dipodium ensifolium | HTCG 1343 | D.M. Crayn 1581 (CNS 145658.1) | AU: QLD; Cook; record is Queensland sensitive |
Dipodium hamiltonianum | HTCG 1683 | D.L. Jones & P.D. Jones s.n. (CANB) | AU: QLD; Moreton; Currimundi |
Dipodium interaneum | HTCG 0181 | J. Egan ORG7745 (CANB) | AU: ACT; Canberra; Birrigai |
Dipodium pandanum 1 | CNS_G01262 | B. Gray 8233 (CANB 572368.2) | AU: QLD; Kennedy North; near Coen; record is Queensland sensitive |
Dipodium pandanum 2 | HTCG 1694 | M. Jacobs 8984 (CANB 576763.1) | PG: Mount Bosavi |
Dipodium pardalinum 1 | HTCG 1684 | D.L. Jones 12834 (CBG 9603749.1) | AU: VIC; Victorian Volcanic Plain; Heathmere |
Dipodium pardalinum 2 | HTCG 1685 | D.L. Jones 12830 (CBG 9603745.1) | AU: VIC; Victorian Volcanic Plain; Heathmere |
Dipodium pulchellum | HTCG 1686 | D.L. Jones s.n. (CANB) | AU: QLD; Moreton; Green Mountains |
Dipodium punctatum | HTCG 0827 | C. Bower ORG7816 (CANB 906469.1) | AU: NSW; Central Tablelands; Black Salee Reserve |
Dipodium roseum 1 | HTCG 1687 | C. Houston ORG3859 (CANB 656733.1) | AU: SA; Lofty South; Wotton Scrub |
Dipodium roseum 2 | HTCG 1688 | C. Houston ORG3859 (CANB 656733.2) | AU: SA; Lofty South; Wotton Scrub |
Dipodium stenocheilum 1 | HTCG 1689 | M.A. Clements 1189 (CBG 7801007.1) | AU: NT; Darwin and Gulf; Elcho Island |
Dipodium stenocheilum 2 | HTCG 1690 | D.E. Murfet 3018 (CANB 619696.1) | AU: NT; Darwin and Gulf; Livingston |
Dipodium variegatum | HTCG 1692 | D.L. Jones 1280 (CANB 665182.1) | AU: QLD; Moreton; Beenleigh |
Outgroup | |||
Acriopsis emarginata | CNS_G00305 | C.D. Kilgour 634A (CNS 135324.1) | AU: QLD, Cook, Daintree National Park |
Cymbidium canaliculatum | CNS_G00165 | K.R. McDonald, 11722 (BRI AQ0831415) | AU: QLD, Cook, Mungkan Kandju National Park |
Eulophia bicallosa | HTCG 1696 | I. Morris (DLJ 4579) (CBG 8913381.1) | AU: NT; Darwin and Gulf; Howard Springs |
Eulophia graminea | CNS_G02766 | C.P. Brock 311 (CANB 596921.1) | AU: NT; Darwin |
Eulophia nuda | HTCG 1697 | R. Crane 1072 (CANB) | cult. ex AU: QLD; Moreton; Caloundra |
Geodorum densiflorum | CNS_G01890 | K. Schulte 254B (CNS 146066.1) | AU: QLD; Cairns region |
Oeceoclades pelorica | HTCG 1695 | J. Taylor s.n. (CBG 7905124.1) | cult. ex AU: QLD; Cook; Iron Range |
Taxonomy according to the Australian Plant Census (APC, 2023). CANB, Australian National Herbarium; CNS, Australian Tropical Herbarium; AU, Australia; PG, Papua New Guinea; ACT, Australian Capital Territory; NT, Northern Territory; NSW, New South Wales; SA, South Australia; QLD, Queensland; WA, Western Australia; VIC, Victoria.
2.2. DNA extraction, library preparation, and sequencing
Standard plant DNA extractions were carried out from 5–20 mg of silica-dried plant tissue from field collections or herbarium material ( Table 1 ) at the National Research Collections Australia (NRCA; CSIRO) in Canberra. The Invisorb DNA Plant HTS96 kit (Stratec, Birkenfeld, Germany) was used following the manufacturer’s protocol, with a final elution of 60 µL.
DNA of Dipodium samples ( Table 1 ) was sonicated to an average target length of ca. 200 base pairs (bp) using a LE220 sonicator (Covaris, Bankstown, Australia). After sonication, DNA length and concentration were quantified on Fragment Analyzer (Agilent Technologies, Santa Clara, CA, USA) using the Agilent high-sensitivity genomic DNA kit.
DNA libraries were prepared using the QiaSeq UltraLow Input library kit (Qiagen, Germantown, Australia) using custom dual-indexed adapters. Final libraries were size-selected on Fragment Analyzer using the high-sensitivity Genomic Fragment Analyzer Kit (Agilent, Santa Clara, CA, USA), quantified using the Fluoroskan plate fluorometer (Thermo Fisher, Waltham, MA, USA) and the Quant-iT HS dsDNA kit (Invitrogen, Carlsbad, CA, USA) following the manufacturer’s instructions. Samples were pooled equimolarly and sequenced using 150 bp paired-end reads on a NovaSeq S1 flowcell (Illumina, San Diego, CA, USA) at the Biomolecular Resource Facility within the John Curtin School of Medical Research, Australian National University (Canberra, Australia). For some samples (prefixed CNS), DNA libraries were prepared using the TruSeq Nano DNA LT library preparation kit (Illumina, San Diego, CA, USA) with an insert size of 350 bp, following the manufacturer’s protocols. Pooled libraries (96x) were sequenced on an Illumina HiSeq 2500 platform with 125 bp paired-ends at the Australian Genomic Research Facility, Melbourne (Australia).
2.3. Data processing and whole plastid genome assembly
Both de novo and reference-guided assemblies were carried out for the Dipodium dataset. Trimming and assembly of de novo contigs were carried out as described by Nargar et al. (2022). Briefly, raw sequences were trimmed by applying a Phred score >20 using Trimmomatic 0.39 (Bolger et al., 2014) and deduplicated using “clumpify” from BBtools 38.9 (Bushnell, 2014). Read pairs were de novo assembled using SPAdes 3.15 (Bankevich et al., 2012) and GetOrganelle (v1.7.7.0) (Jin et al., 2020) using default settings. Plastid databases were extracted from the National Center for Biotechnology Information (NCBI) Nucleotide Entrez database using Entrez Programming Utilities (2008) using taxonomic, keyword, and sequence length constraints. Contigs were identified as derived from plastid source using blastn against these databases. Genes within plastid contigs were identified by homology using BLAST (Altschul et al., 1990) and BLASTx (RRID: SCR_001653) against genes extracted from annotations of the reference sequence sets extracted from nuccore.
Reference-guided assemblies were performed with paired, merged reads and the recently published and closely related plastome of D. roseum D.L. Jones and M.A. Clem. (MN200386, Kim et al., 2020). The related orchid Masdevallia coccinea Linden ex Lindl. (KP205432, Kim et al., 2015) was included as an additional reference sequence to ensure that regions that already showed degradation in some plastid genes in the plastome of D. roseum (e.g., all ndh genes) (MN200386, Kim et al., 2020) and which may still be present in other Dipodium species could be assembled, as the plastome of M. coccinea has a full set of functional plastid genes (Kim et al., 2015).
Reference-guided assemblies were carried out using the plugin “map to reference” in Geneious Prime (Version 2022.0.2, Biomatters Ltd., www.geneious.com) with default settings. To obtain complete plastome assemblies, consensus sequences for each sample were extracted (threshold 60%, reading depth >10), aligned using MAFFT v7.388 (Katoh and Standley, 2013) in Geneious, manually checked, and compared. Reference-guided assemblies were visually inspected and compared to de novo assemblies obtained with SPAdes and GetOrganelle based on alignments generated with MAFFT v7. 388 in Geneious. In cases of misassembled regions due to potential mismatches between the sample and the reference plastome in reference-guided assemblies, de novo assemblies were consulted and the region extracted from the de novo assembly were quality allowed. The prediction and finding of gene annotations for complete plastome assemblies were performed using the Geneious plugin “predict annotation” [similarity, 90%; best match with D. roseum (MN200386)]. Open reading frames (ORFs) were manually checked and verified by identifying the start and stop codons. In cases of remaining ambiguities, BLAST searches were conducted for reading-frame verification (Altschul et al., 1990). The IR boundaries were identified using the “repeat finder” plugin in Geneious with default settings.
In total, 24 complete Dipodium plastomes were assembled in this study and are available in the CSIRO Data Access Portal (DOI: https://doi.org/10.25919/6wcx-0h88). The graphical representation of each plastome and divergent regions with annotations was created using OrganellarGenomeDRAW (OGDRAW, version 1.3.1, Greiner et al., 2019).
2.4. Phylogenetic analyses
To elucidate phylogenetic relationships within Dipodium and to assess the phylogenetic position of Dipodium within Cymbidieae, we performed a phylogenetic analysis with DNA sequences of 33 newly sequenced plastomes from this study ( Table 1 ) and an extended outgroup sampling for 115 samples from published plastid data ( Supplementary Material 1 ).
Coding regions of the respective genes of 33 samples were extracted using the “extract” function in Geneious Prime. Where mutations had led to frameshifts with internal stop codons, the affected sequences were excluded from phylogenetic analyses.
Each extracted coding region of a total of 68 plastid loci from 33 samples (including the intron regions) and 115 published plastomes (excluding intron regions) were aligned using MAFFT Geneious prime plugin (v7.388; Katoh et al., 2002; Katoh and Standley, 2013) with default settings, checked manually, and subsequently concatenated to an alignment of 69,335 bp ( Supplementary Material 2 ).
Maximum likelihood analysis of the plastid dataset (148 samples) with best-fit models GTR+I+I+F+R4 and partitioning schemes of ModelFinder was performed using IQ-TREE ver. 2.2.0 (Nguyen et al., 2015; Kalyaanamoorthy et al., 2017; Minh et al., 2020). Branch support was obtained with the Shimodaira-Hasegawa-like approximate Likelihood Ratio Test (SH-aLRT; Guindon et al., 2010) and the ultrafast bootstrap (ufboot2; Hoang et al., 2018) as implemented in the IQ-TREE software. The tree topology was visualised using the software Figtree (ver. 1.4.4.; http://tree.bio.ed.ac.uk/software/figtree/).
2.5. Divergence-time analysis
For divergence-time estimations of Dipodium, the alignments were reduced to the 30 most parsimony-informative loci due to computational limitations. The 30 plastid loci were selected based on their most parsimony-informative (Pi) sites estimated using MEGA (Molecular Evolutionary Genetics Analysis; ver. 11.0.11, Tamura et al., 2021) and the presence of loci across the dataset ( Supplementary Material 2 ). For taxa represented by more than one sample, duplicates were removed from alignments as recommended for divergence-time estimation. Alignments of 30 plastid loci from 134 taxa were concatenated, yielding a total alignment length of 27,934 bp using MAFFT (v7.388; Katoh et al., 2002; Katoh and Standley, 2013) implemented in Geneious Prime ( Supplementary Material 2 ). Absolute node ages and phylogenetic relationships were jointly estimated in BEAST (ver. 2.7.4; Bouckaert et al., 2014, 2019), applying the best-fit model as determined by IQ-TREE’s ModelFinder (GTR+F+I+I+R4). Four different models were tested: a Bayesian optimised relaxed and a strict molecular clock with uncorrelated lognormal rates with each a Yule and a birth–death tree prior to the speciation process (Yule, 1925; Zuckerkandl and Pauling, 1965; Gernhard, 2008; Douglas et al., 2021). Trees were calibrated with four secondary calibration points based on Zhang et al. (2023). A normal distribution with an offset value of 101.52 Ma and a standard deviation (SD) of 2.2 was assigned as the crown age of Orchidaceae. The priors for the three other calibration points were set with a normal distribution and the means of stem ages for Vanilloideae (offset value = 93.48 Ma, SD = 2.7), Cypripedioideae (offset value = 89.14 Ma, SD = 2.71), and Orchidoideae (offset value = 77.74 Ma, SD = 2.0). For each clock model, 10 parallel BEAST analyses with each 30 million generations and a sampling frequency of every 10,000 generations were carried out. The run parameters were examined in TRACER (ver. 1.7.2; Rambaut et al., 2018), and the effective sample sizes (ESSs) of >200 for all parameters and the burn-in were assessed. The runs were combined in LogCombiner (Drummond and Rambaut, 2007) with a burn-in of 10% and subsequently used to generate a maximum-clade-credibility chronogram with mean node heights in TreeAnnotator (Drummond and Rambaut, 2007). To determine the best fitting clock model and speciation models for the dataset, a model comparison using the Akaike information criterion by Markov chain Monte Carlo (MCMC) (AICM) was performed using BEAST v.2.6.2 and evaluated using the AIC model selection criterion of Fabozzi et al. (2014).
2.6. Plastid genome evolution
2.6.1. Structural variation in Dipodium plastomes
To examine structural variation among the plastomes of Dipodium, whole plastome alignments were generated using MAFFT (v7.388; Katoh et al., 2002; Katoh and Standley, 2013) implemented in Geneious Prime with full annotations. Alignments were manually checked, in cases of divergent regions, e.g., the operon region of ndhC, ndhK, and ndhJ genes or junctions between the large single copy (LSC)/inverted repeat B (IRB)/SSC/inverted repeat A (IRA) regions; respective regions (including annotations) were extracted in Geneious Prime, separately aligned, proofread, and subsequently visualised using OGDRAW (ver. 1.3.1, Greiner et al., 2019).
2.6.2. Functional genes, pseudogenes, and physical gene loss
To classify the level of degradation of plastid genes in Dipodium, we used the following categories. 1) Functional: The reading frame was intact, and less than 10% of the open reading frame was disrupted by small indels. 2) Moderately pseudogenised: Less than 10% of the open reading frame was disrupted by internal stop codons or indels, causing non-triplet frameshifts. 3) Severely pseudogenised: More than 10% of the open reading frame was disrupted by internal stop codons, large deletions (>10%), or non-triplet frameshifts (based on Barrett et al., 2019). 4) Lost: The gene was not identified in the annotation process of the de novo assembly (e.g., Joyce et al., 2018) and/or was not detectable within the reference-guided assembly. A gene was considered as not detectable within the reference-guided mapping process if at least 70% of the gene sequence could not be identified for calculation of the consensus sequence within the Geneious mapping process. The coded matrix of gene degradation was plotted against the maximum likelihood phylogenetic tree of Dipodium.
3. Results
3.1. Phylogenetic placement of Dipodium in tribe Cymbidieae and infrageneric relationships within the genus
The maximum likelihood analysis based on 68 plastid loci and 148 samples yielded highly resolved and well-supported tree topologies for the phylogenomic relationships within Orchidaceae ( Supplementary Material 3 ). Within Epidendroideae, Cymbidiinae was monophyletic and sister to all other Cymbidieae including Dipodiinae (SH-aLRT/UFboot 100/100; Figure 2 ). Dipodium was retrieved as the next diverging lineage within Cymbidieae and monophyletic with maximum support values (SH-aLRT/UFboot 100/100; Figure 2 ).
Within Dipodium, section Leopardanthus was placed as a sister group to section Dipodium with maximum support values (SH-aLRT/UFboot 100/100; Figure 3 ). Section Dipodium was resolved as monophyletic and divided into six highly supported lineages. The leafy species D. ensifolium was placed as a sister to all leafless species of the section (SH-aLRT/UFboot 100/100; Figure 3 ). Next, sect. Dipodium was split into two main clades, A and B (SH-aLRT/UFboot 99/100; Figure 3 ). Clade A split into two lineages, the D. hamiltonianum complex and the D. stenocheilum complex, receiving maximum nodal support (SH-aLRT/UFboot 100/100; Figure 3 ). The D. hamiltonianum complex comprised the two species, D. hamiltonianum and D. interaneum. The D. stenocheilum complex included D. ammolithum, D. basalticum, D. elegantulum, D. stenocheilum, and D. aff. stenocheilum. D. stenocheilum was retrieved as non-monophyletic ( Figure 3 ).
Clade B resolved D. variegatum as a sister to the remaining species of the clade (SH-aLRT/UFboot 100/100). The remainder was split into the D. punctatum complex and the D. roseum complex (SH-aLRT/UFboot 99.7/100; Figure 3 ). The D. punctatum complex comprised three species, D. campanulatum, D. pulchellum, and D. punctatum. The phylogenetic divergence between these three species was shallow and supported by interspecific relationships within the complex low. The D. roseum complex comprised four taxa, namely, D. atropurpureum, D. pardalinum, D. roseum, and D. aff. roseum. Resolution and support for interspecific relationships within the D. roseum complex were low overall.
3.2. Divergence-time estimations
Absolute times of divergence under strict and optimised relaxed clocks for Orchidaceae based on 30 plastid loci and 134 taxa showed similar results. Strict clock models consistently yielded slightly older age estimates than the analyses based on the relaxed clock models ( Supplementary Material 4 ). Model comparison using AICM (Fabozzi et al., 2014) identified the relaxed clock model under the birth–death speciation model as the best-fit model for the dataset ( Supplementary Material 4 ).
The Bayesian relaxed clock tree topology and the maximum likelihood phylogeny agreed overall in major relationships within Orchidaceae and the placement of species within Dipodium. Epidendroideae was estimated to have emerged ca. 77.7 Ma [highest posterior density (HDP), 74.2–81.5] with the stem age of subtribe Cymbidieae placed in the Eocene, ca. 42.2 Ma (HDP, 34.3–50.1) ( Supplementary Materials 4 , 5 ). The stem age of subtribe Cymbidiinae, the first diverging lineage in Cymbidieae, was placed in the late Eocene, ca. 38.0 Ma (HDP, 30.7–45.7) ( Figure 4 ). Stem diversification of Dipodiinae was estimated to have commenced ca. 33.3 Ma (HDP, 26.4–40.6) in the early Oligocene ( Figure 4 ). Crown diversification of Dipodiinae was estimated to have commenced much later, in the late Miocene with sections Dipodium and Leopardanthus diverging ca. 11.3 Ma (HDP, 6.8–16.2) ( Figure 4 ). The crown age of section Dipodium was estimated to be ca. 8.1 Ma (HDP, 5.2–11.6) in the late Miocene with the divergence of the leafy species, D. ensifolium, from the remainder of section Dipodium ( Figure 4 ). The crown age of the remainder of the section, i.e., all leafless species, was estimated to be ca. 7.3 Ma (HDP, 4.4–10.4) ( Figure 4 ). Within this leafless clade, two subclades, each containing two species complexes, were resolved. The crown age of the clade comprising the D. hamiltonianum complex and the D. stenocheilum complex was estimated to be ca. 4.3 Ma (HDP, 2.5–6.4) in the early Pliocene ( Figure 4 ), which is congruent with estimations of the crown age of clade B (comprising D. variegatum and the two complexes D. punctatum and D. roseum) ( Figure 4 ). The D. stenocheilum complex had a crown age of ca. 2.4 Ma (HDP, 1.3–3.6) in the early Pleistocene. The three remaining complexes had crown ages estimated to the mid-Pleistocene (D. hamiltonianum complex, ca. 0.7 Ma, HDP, 0.1–1.4; D. punctatum complex, ca. 0.6 Ma, HDP, 0.2–1.0, and D. roseum complex, ca. 0.7 Ma, HDP, 0.3–1.3) ( Figure 4 ).
3.3. Characterisation of Dipodium plastomes
Complete reference-guided plastome assemblies and annotations were successfully carried out for 24 Dipodium samples, representing all Australian species of section Dipodium including two recently discovered species of section Dipodium (D. ammolithum and D. basalticum), two putatively new species of section Dipodium (D. aff. roseum and D. aff. stenocheilum), and one species of section Leopardanthus (D. pandanum) ( Table 2 ). However, de novo assemblies using SPAdes and GetOrganelle often did not yield complete circular plastomes ( Supplementary Material 6 ). Two successful complete de novo assemblies (the leafy D. pandanum 1 and the leafless D. atropurpureum 1) as well as partial contigs from other de novo assemblies were compared to the respective reference-guided assembled plastomes. In the two complete de novo assembled plastomes (D. pandanum 1 and D. atropurpureum 1) and the respective reference-guided plastomes, no fundamental structural differences were detected. Minor discrepancies concerned some degraded plastid loci (mainly ndh genes). In these degraded plastid loci, bases tended to be recovered to a slightly greater extent in the reference-guided assemblies compared to de novo assemblies. These general findings agreed with the comparison of partial contigs from the de novo assemblies for most other samples to the respective reference-guided assembled plastomes. Plastome assemblies for D. pandanum 2 and D. aff. stenocheilum showed an insufficient mean coverage (<30) for non-coding regions, which caused unsolved gaps and ambiguous bases that could not be reliably resolved with the reference-guided or de novo assemble approaches. The number of paired-end trimmed reads for the successfully reference-guided assembled complete plastomes ranged from 332,604 (D. pandanum 1) to 27,999,734 (D. pardalinum 2), and the mean coverage ranged from 31x to 627x ( Supplementary Material 6 ).
Table 2.
Sample | Plastome length (bp) | SSC length (bp) | IRA/B length (bp) | LSC length (bp) | GC content | Total CDS (unique CDS) | Total tRNA (unique tRNA) | Total rRNA (unique rRNA) | Total pseudogenes | Total lost genes | Total functional genes |
---|---|---|---|---|---|---|---|---|---|---|---|
D. pandanum 1 | 146,204 | 13,849 | 24,762 | 82,831 | 37.0% | 74 (68) | 38 (30) | 8 (4) | 9 | 3 | 120 |
D. ensifolium | 150,084 | 16,756 | 25,497 | 82,334 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 10 | 3 | 120 |
Dipodium hamiltonianum complex | |||||||||||
D. hamiltonianum | 145,902 | 14,384 | 24,929 | 81,660 | 37.1% | 74 (68) | 39 (31) | 8 (4) | 10 | 3 | 121 |
D. interaneum | 146,497 | 14,635 | 24,951 | 81,960 | 37.0% | 74 (68) | 39 (31) | 8 (4) | 10 | 3 | 121 |
Dipodium stenocheilum complex | |||||||||||
D. elegantulum | 144,865 | 14,003 | 24,606 | 81,650 | 36.9% | 74 (68) | 39 (31) | 8 (4) | 9 | 4 | 121 |
D. stenocheilum 2 | 145,589 | 13,821 | 25,127 | 81,514 | 37.0% | 74 (68) | 39 (31) | 8 (4) | 9 | 4 | 121 |
D. stenocheilum 1 | 144,751 | 12,670 | 25,009 | 82,063 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 9 | 4 | 120 |
D. basalticum | 148,478 | 15,238 | 25,640 | 81,960 | 37.0% | 74 (68) | 38 (30) | 8 (4) | 10 | 3 | 120 |
D. ammolithum | 147,842 | 14,697 | 25,600 | 81,946 | 37.0% | 74 (68) | 39 (31) | 8 (4) | 9 | 4 | 121 |
D. variegatum | 142,949 | 12,039 | 24,436 | 82,038 | 37.0% | 74 (68) | 38 (30) | 8 (4) | 6 | 7 | 120 |
Dipodium punctatum complex | |||||||||||
D. pulchellum | 151,425 | 15,735 | 26,369 | 82,952 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 11 | 2 | 120 |
D. punctatum | 151,181 | 15,737 | 26,136 | 83,172 | 37.0% | 74 (68) | 38 (30) | 8 (4) | 11 | 2 | 120 |
D. campanulatum 1 | 146,390 | 13,602 | 25,284 | 82,220 | 36.9% | 74 (68) | 37 (29) | 8 (4) | 12 | 2 | 119 |
D. campanulatum 2 | 149,050 | 14,266 | 25,902 | 82,980 | 37.0% | 74 (68) | 38 (30) | 8 (4) | 11 | 2 | 120 |
Dipodium roseum complex | |||||||||||
D. atropurpureum 2 | 149,390 | 15,509 | 25,909 | 82,063 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 10 | 3 | 120 |
D. atropurpureum 1 | 150,481 | 15,633 | 26,399 | 82,050 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 9 | 4 | 120 |
D. aff. roseum 4 | 152,282 | 16,426 | 26,630 | 82,596 | 36.9% | 73 (67) | 38 (30) | 8 (4) | 11 | 3 | 119 |
D. aff. roseum 2 | 150,462 | 15,514 | 26,388 | 82,172 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 9 | 4 | 120 |
D. aff. roseum 3 | 152,956 | 16,571 | 26,817 | 82,751 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 10 | 3 | 120 |
D. aff. roseum 1 | 151,791 | 16,362 | 26,424 | 82,581 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 10 | 3 | 120 |
D. pardalinum 2 | 151,659 | 16,276 | 26,580 | 82,223 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 10 | 3 | 120 |
D. pardalinum 1 | 148,174 | 15,283 | 25,494 | 81,903 | 36.8% | 74 (68) | 38 (30) | 8 (4) | 9 | 4 | 120 |
D. roseum 1 | 150,857 | 15,848 | 26,521 | 81,967 | 36.9% | 74 (68) | 38 (30) | 8 (4) | 9 | 4 | 120 |
D. roseum 2 | 147,730 | 14,192 | 25,819 | 81,900 | 36.8% | 74 (68) | 38 (30) | 8 (4) | 9 | 4 | 120 |
3.3.1. Plastome features and structural variations within Dipodium plastomes
Plastome sizes of Dipodium ranged from 142,949 bp (D. variegatum) to 152,956 bp (D. aff. roseum 3) ( Table 2 , Figure 5 ; Supplementary Material 7 ). The largest average plastome size (150,578 bp) was found in the D. roseum complex, closely followed by the leafy D. ensifolium (150,084 bp) and the D. punctatum complex (149,512 bp). Plastome sizes within the D. stenocheilum complex were markedly lower with an average size of 146,305 bp. Similarly, small plastomes were also found in D. hamiltonianum (145,902 bp), D. interaneum (146,497 bp), and the leafy climber D. pandanum 1 (sect. Leopardanthus) (146,204 bp) ( Table 2 ). Dipodium plastomes possess the typical quadripartite structure of angiosperms, with the SSC region ranging from 12,039 bp (D. variegatum) to 16,756 bp (D. ensifolium), the LSC region ranging from 81,514 bp (D. stenocheilum 2) to 83,172 bp (D. punctatum), and the pair of IRs ranging from 24,436 bp (D. variegatum) to 26,817 bp (D. aff. roseum 3) ( Table 2 ).
Total mean GC content of Dipodium plastomes was 36.9%, ranging between 36.8% (D. roseum 2 and D. pardalinum 1) and 37.1% (D. hamiltonianum) ( Table 2 ). Within the D. roseum complex, the GC content was 36.8%–36.9%, followed by the D. punctatum complex (36.9%) and D. stenocheilum complex (37.0%), and the highest GC content was 37.1% and 37.0% (D. hamiltonianum and D. interaneum, respectively) ( Table 2 ).
The plastid genes of each plastome were rated as functional, moderately to severely pseudogenised, or physically lost. The total number of functional genes in Dipodium plastomes ranged slightly from 119 to 121, including a total of 73 or 74 functional protein-coding sequence regions [protein-coding sequence (CDS)] (68 or 69 unique CDS), 37 to 39 functional tRNA genes (30 or 31 unique tRNA genes), and eight rRNA genes (four unique rRNA genes) ( Table 2 ).
The IR region was largely conserved among all examined Dipodium plastomes. All species showed six duplicated coding regions in the IRs (i.e., rpl2, rpl23, rps7, rps12, rps19, and ycf2) and all four rRNA genes ( Table 3 ). Most plastomes showed eight duplicated tRNA genes in the IR regions with the exception of the plastomes of D. interaneum and D. elegantulum, which comprised a duplicated trnV-GAC within the IRB, and the plastomes of D. ammolithum, D. hamiltonianum, and D. stenocheilum 2, which contained a duplicated trnV-GAC within the IRA ( Table 3 , Figures 5B, C ). All plastomes contained 16 functional intron genes (i.e., atpF, clpP, petB, petD, rpl2, rpl16, rpoC1, rps12, rps16, trnA-UGC, trnG-UCC, trnI-GAU, trnK-UUU, trnL-UAA, trnV-UAC, and ycf3), except for D. pandanum 1, which possessed two pseudogenes with introns (i.e., ndhA and ndhB) ( Table 3 , Figure 5 ). The rps12 gene was trans-spliced with the 5′ end located in the LSC region, and the 3′ end was duplicated in the IRs in all studied plastomes ( Figure 5 ; Supplementary Material 7 ).
Table 3.
Gene group | Gene name |
---|---|
Transfer RNA genes | trnA-UGC* a , trnC-GCA, trnD-GUC d , trnE-UUC, trnF-GAA, trnfM-CAU, trnG-GCC, trnG-UCC*, trnH-GUG a , trnI-CAU a , trnI-GAU* a , trnK-UUU*, trnL-CAA a , trnL-UAA*, trnL-UAG, trnM-CAU, trnN-GUU a , trnP-UGG, trnQ-UUG, trnR-ACG a , trnR-UCU, trnS-GCU, trnS-GGA, trnS-UGA, trnT-GGU, trnT-UGU, trnV-GACab, trnV-UAC*, trnW-CCA, trnY-GUA |
Small subunit of ribosome | rps2, rps3, rps4, rps7 a , rps8, rps11, rps12* a , rps14, rps15, rps16*, rps18, rps19 a |
Large subunit of ribosome | rpl2* a , rpl14, rpl16*, rpl20, rpl22, rpl23 a , rpl32, rpl33, rpl36 |
DNA-dependent RNA polymerase | rpoA, rpoB, rpoC1*, rpoC2 |
Genes for photosynthesis | |
Subunits of photosynthesis I | psaA, psaB, psaC, psaI, psaJ |
Subunits of photosynthesis II | psbA, psbB, psbC, psbD, psbE, psbF, psbH, psbI, psbJ, psbK, psbL, psbM, psbN, psbT, psbZ |
Subunit of Cytochrome b6f | petA, petB*, petD*, petG, petL, petN |
Subunit of ATP synthase | atpA, atpB, atpE, atpF*, atpH, atpI |
Subunit of NADH dehydrogenase | ndhA* c , ndhB*ac, ndhC c , ndhD c , ndhE c , ndhF c , ndhG c , ndhH c , ndhI c , ndhJ c , ndhK c |
Large subunits of RubisCO | rbcL |
Ribosomal RNA genes | rrn5 a , rrn4.5 a , rrn16 a , rrn23 a |
Other genes | |
Maturase | matK |
Envelope membrane protein | cemA e |
Subunit of acetyl-CoA carboxylase | accD |
C-type cytochrome synthesis gene | cssA |
Protease | clpP* |
Translation initiation factor IF-1 | infA |
ycf genes | ycf1, ycf2 a , ycf3*, ycf4 |
Duplicated gene.
Triplicated gene in D. hamiltonianum, D. interaneum, D. elegantulum, D. stenocheilum 2, and D. ammolithum.
Pseudogene or lost.
Pseudogene in D. campanulatum 1.
Pseudogene in D. aff. roseum 4.
*Intron-containing gene.
The SSC region was found to vary the most among the examined samples. All plastomes showed a contraction of the SSC with a reduction of 20%–40% compared to the average size of the angiosperm SSC regions (ca. 20 kb) (Ruhlman and Jansen, 2014).
Three plastomes (D. pandanum 1, D. stenocheilum 1, and D. variegatum) lost the ndhF gene. This complete loss of the ndhF gene resulted in the ycf1 fragment being located in the vicinity of the rpl32 ( Figures 5B–D ) and caused a boundary shift of the IRB/SSC region located at the 3′ end of the ycf1 fragment and spacer region of rpl32 ( Figure 5 ). All other plastomes exhibited a severely truncated ndhF gene but did not exhibit an IRB/SSC boundary shift ( Figure 5 ; Supplementary Material 7 ). The IRA/SSC junction in all examined plastomes was located within the 5′ portion of the functional ycf1 gene, ranging from 97 bp (D. pandanum 1) to 1,072 bp (D. aff. roseum 3) ( Figure 5 ).
In contrast to the instability of the IR/SSC boundaries, IR/LSC boundaries were found to be relatively stable. For all studied plastomes, the LSC/IRA boundaries were located near the 3′ end of psbA ( Figure 5 ). Variations within the LSC regions were limited to the operon, which contained ndhC, ndhJ, ndhK ( Figure 5A ), and the independent pseudogenisation of cemA in the plastome of D. aff. roseum 4 and trnD-GUC in the plastome of D. campanulatum ( Table 3 ; Supplementary Material 7 ).
3.3.2. ndh gene degradation and loss in Dipodium
All ndh genes exhibited varying degrees of putative loss or pseudogenisation; not a single ndh gene remained functional in the examined Dipodium plastomes ( Table 3 , Figures 5 , 6 ).
The most severe ndh gene loss occurred in the plastome of D. variegatum, with ndhA, ndhB, ndhD, and ndhK severely pseudogenised and ndhJ moderately pseudogenised.
The greatest degradation processes within Dipodium occurred for the ndhG gene, which was putatively lost in almost all plastomes, except D. stenocheilum 1, which retained a severely pseudogenised ndhG gene ( Figure 6 ). This was followed by ndhK, which was lost in 19 out of 24 plastomes (D. ensifolium, D. hamiltonianum, D. interaneum, the D. roseum complex, and the D. stenocheilum complex) ( Figure 6 ). In the six remaining plastomes, ndhK was conserved to different degrees. D. punctatum, D. pulchellum, and D. campanulatum 2 retained more than 90% of the homologous bases compared to the functional ndhK gene of M. coccinea (KP205432, Kim et al., 2015) but showed severe frameshift mutations and indels, which caused several internal stop codons. The plastomes with severely pseudogenised ndhK genes exhibited large truncations.
Nine Dipodium samples (D. ammolithum, D. atropurpureum 1, D. elegantulum, D. pardalinum 1, D. roseum 1 and 2, D. aff. roseum 2, D. stenocheilum 2, and D. variegatum) putatively lost the ndhC gene. In D. punctatum, ndhC was moderately pseudogenised, and in the remaining plastomes, ndhC was severely pseudogenised ( Figure 6 ). Only D. ensifolium showed an intact start codon for the ndhC gene but suffered a severe truncation with the loss of ca. 50% of homologous bases compared to the functional ndhC gene of M. coccinea (KP205432, Kim et al., 2015).
In D. pandanum 1, D. stenocheilum 1, and D. variegatum, the ndhF gene was putatively lost ( Figure 6 ). All other samples possessed severely truncated ndhF genes with absent start codons and multiple internal stop codons. The ndhH gene was present in D. pandanum 1, possessing a length of 1,176 bp (99.2% of homologous length compared to M. coccinea; KP205432, Kim et al., 2015). In most other samples, the ndhH gene was degraded, possessing several stop codons. D. stenocheilum 1 and D. variegatum lost the ndhH gene ( Figures 5 , 6 ).
Moreover, ndhE, ndhI, and ndhA were found to be putatively lost in the plastome of D. variegatum and D. pandanum 1 ( Figures 5 , 6 ). No gene loss occurred for ndhB, ndhD, and ndhJ; however, all three genes exhibited various degrees of degradation within all examined Dipodium plastomes and were either moderately or severely pseudogenised due to internal stop codons or frameshift mutations.
The ndhD gene was found to have undergone the fewest degradation processes in regard to gene length, which was largely conserved ranging from 1,122 bp (D. campanulatum 1) to 1,521 bp (D. pulchellum), and in most plastomes, ndhD possessed the alternative start codon ACG (Threonine). Furthermore, almost all Dipodium plastomes showed the canonical AUG (Methionine) start codon for ndhA, ndhB, ndhE, and ndhI. The intron-containing ndhA and ndhB genes exhibited the strongest degradation (i.e., large deletions) within the intron regions and the downstream exon in all Dipodium samples. Exon1 of ndhB was almost complete and in-frame for most plastomes and showed only one point mutation (from A to C), which resulted in a stop codon at amino acid position 68 (after 201 bp from the beginning of the first exon in ndhB).
Within different Dipodium complexes, the patterns for putative ndh gene losses and severe or moderate pseudogenisations were similar for examined plastomes of D. hamiltonianum and D. interaneum. Both plastomes putatively lost ndhG and ndhK and showed severe pseudogenisations of ndhA, ndhB, ndhC, ndhF, ndhH, and ndhJ and a moderately pseudogenised ndhE gene, but differed in the level of putative pseudogenisation of ndhD and ndhI ( Figure 6 ).
Other similarities were found in the D. roseum complex, in which the ndhD gene was moderately pseudogenised in all samples. Almost all samples of the D. roseum complex, except for D. roseum 2, harboured moderately pseudogenised ndhE and ndhI genes.
Within the same species, only D. aff. roseum 3 and D. aff. roseum 4 showed the same pattern of ndh gene loss and level of degradation, which was also present in the plastome of D. pardalinum 2. Within the D. stenocheilum complex, D. stenocheilum 1 putatively lost ndhI and ndhF.
Across other samples, only two plastome pairs (D. ensifolium and D. aff. roseum 1; D. basalticum and D. atropurpureum 2) shared the same pattern of ndh gene loss and degradation. In comparison to all other species of examined Dipodium plastomes, D. variegatum independently lost ndhE and ndhI, and D. pandanum 1 lost the ndhA gene ( Figure 6 ).
4. Discussion
4.1. Phylogenetic placement and infrageneric relationships of Dipodium
This phylogenomic study based on 68 plastid loci provided strong support for the monophyly of Dipodium and its phylogenetic placement as an early diverging lineage within the tribe Cymbidieae. Previous phylogenetic studies included only one or two species of Dipodium, which precluded assessment of the monophyly of the genus (Pridgeon et al., 2009: Górniak et al. (2010); Batista et al. (2014); Chase et al., 2015; Freudenstein and Chase (2015); Kim et al., 2020; Serna-Sánchez et al., 2021; McLay et al., 2023; Pérez-Escobar et al., 2023). Our study resolved Dipodium as diverging early within Cymbidieae after subtribe Cymbidiinae with strong support and thus confirmed previous molecular phylogenetic studies in support of recognition of Dipodium at subtribal level as Dipodiinae (Li et al., 2016; Kim et al., 2020; Serna-Sánchez et al., 2021; Pérez-Escobar et al., 2023).
This phylogenomic study presents the first molecular evidence in support of the infrageneric classification of Dipodium into sect. Dipodium and sect. Leopardanthus (O’Byrne, 2014, 2017; Jones, 2021), lending support to the diagnostic value of vegetative traits (i.e., the presence or absence of adventitious roots) in the infrageneric classification of Dipodium. Section Leopardanthus is characterised by leafy species, which possess adventitious roots, such as D. pandanum. In contrast, sect. Dipodium comprises species without adventitious roots and includes all leafless species, the leafy species D. ensifolium, and the morphologically similar D. gracile from Sulawesi, the latter being only known from the type (destroyed) (O’Byrne, 2017). Our phylogenomic study supported the placement of the D. ensifolium in sect. Dipodium, resolved as sister to all leafless species in the section. However, further molecular study is warranted to ascertain the monophyly of the two sections based on an expanded sampling of sect. Leopardanthus.
Our phylogenomic study is the first to shed light on evolutionary relationships within sect. Dipodium, which was found to comprise six main lineages. The phylogenomic framework now allows the assessment of useful diagnostic morphological traits to characterise main lineages within the section. For example, the yellow stem and flower colour of species of the D. hamiltonianum complex easily distinguishes this clade from other mycoheterotrophic orchids within sect. Dipodium ( Figure 1 ; Jones, 2021). Stems of remaining mycoheterotrophic species of sect. Dipodium are mostly greenish to dark reddish or purplish, whereas flowers vary in colour from pale white to pinkish and then purplish ( Figure 1 , Jones, 2021; Barrett et al., 2022). Also, sepal and petal characters were found to differ among clades: for example, species of clade A, comprising the D. hamiltonianum and D. stenocheilum complexes, possess sepals and lateral petals that are markedly narrower compared to those of species of clade B (comprising the D. punctatum and D. roseum complex) and D. ensifolium, the first diverging lineage within the sect. Dipodium ( Figures 1 , 3 ) (Jones, 2021; Barrett et al., 2022).
Phylogenetic divergence within the two species complexes in clade B, i.e., the D. punctatum and the D. roseum complexes, was shallow overall, and thus, interspecific relationships in these two groups remained largely unclear ( Figure 3 ). Previous morphological studies highlighted difficulties in species delimitation within the D. punctatum complex, in particular between D. pulchellum and D. punctatum (Jones, 2021). While D. pulchellum is morphologically very similar to D. punctatum, the two species are differentiated by the intensity of their flower colours, which are richer in D. pulchellum and paler in D. punctatum (Jones and Clements, 1987). However, a morphological study by Jones (2021) revealed that the strong floral coloration of D. pulchellum flowers was likely due to differences in environmental factors (i.e., soil type and rainfall regime) of growing sites, and thus, Jones (2021) proposed to synonymise D. pulchellum with D. punctatum.
Similar challenges in taxonomic delimitation based on flower colours are also evident within the D. roseum complex. The distribution of the more widespread species D. roseum largely overlaps with the distributions of D. atropurpureum and D. pardalinum (ALA, 2023). In addition to a very similar growing habit, the flowers of the three species are very similar in shape and vary only slightly in coloration: D. roseum has bright, rosy flowers with small darker spots; D. atropurpureum possesses dark pinkish-purple to dark reddish-purple flowers with spots and blotches; the flowers of D. pardalinum are pale pink to white with large reddish spots and blotches ( Figure 1 ) (Jones, 2021). Taken together, the overlapping distribution, similar appearance, and very shallow genetic divergence found in the present study among species in the D. roseum complex suggest that D. atropurpureum and D. pardalinum may be colour variations of D. roseum. Further molecular study with more highly resolving molecular techniques such as genotyping-by-sequencing is required to rigorously assess species delimitation within Dipodium.
4.2. Divergence-time estimations
Our divergence-time estimations yielded results comparable to those of previous studies regarding the temporal diversification of major orchid clades (e.g., Givnish et al., 2015, 2018; Kim et al., 2020; Serna-Sánchez et al., 2021; Zhang et al., 2023). Within Epidendroideae, this study confirmed that Cymbidieae was one of the most recently diverged tribes in Orchidaceae, consistent with previous studies (e.g., Givnish et al., 2015; Serna-Sánchez et al., 2021; Zhang et al., 2023). Stem and crown diversification of Cymbidieae were estimated to have commenced at ca. 42.2 Ma and 38.0 Ma, respectively, which is similar to the estimates of Serna-Sánchez et al. (2021) and slightly younger than those of Zhang et al. (2023) ( Figure 4 ; Supplementary Materials 4 , 5 ).
Our study is the first to elucidate phylogenetic relationships and divergence times within Dipodium. Previously, only two studies included a representative of Dipodium (D. roseum, MN200368) in divergence-time estimations for Orchidaceae (Kim et al., 2020; Serna-Sánchez et al., 2021). These studies estimated the origin of Dipodium to be ca. 17 Ma and ca. 31 Ma. Our study placed the divergence of Dipodium from the other subtribes in Cymbidieae to ca. 33.3 Ma in the early Oligocene, which is closer to the findings of Serna-Sánchez et al. (2021). O’Byrne (2014) hypothesised that lineage divergence into sect. Dipodium and sect. Leopardanthus resulted from vicariance in conjunction with the break-up of Pangaea, in particular the separation of the Indian and Australian continental plates (O’Byrne, 2014). However, our divergence-time estimations show that Dipodium is far too young (<33 Ma) to have been influenced by the break-up of Pangaea, which occurred from the early Jurassic and onwards. Lineage divergence of sect. Dipodium and sect. Leopardanthus was estimated to be ca. 11.3 Ma in the late Miocene ( Figure 4 ), when Australia had already assumed, approximately, its present geographical position. Rather, Dipodium is likely to have achieved its current distribution through range expansion between Australia and Southeast Asia across the Sunda-Sahul Convergence Zone (Joyce et al., 2021a), consistent with a general pattern of floristic exchange—the Sunda-Sahul Floristic Exchange—which was initiated as early as ca. 30 Ma (Crayn et al., 2015; Joyce et al., 2021b). However, the data are insufficient at present to resolve the ancestral area of Dipodium and its main lineages. Further research is needed including an increased sampling to shed light on the range evolution of Dipodium through ancestral range reconstruction.
Our results indicate that the Australian leafy species D. ensifolium diverged from the remainder of section Dipodium approximately 8.1 Ma (late Miocene) ( Figure 4 ). The remainder of the sect. Dipodium clade, which includes all leafless, putatively fully mycoheterotrophic species, emerged ca. 7.3 Ma (late Miocene) followed by rapid diversification from ca. 4.3 Ma onwards (early Pliocene) ( Figure 4 ). Thus, mycoheterotrophy has most likely evolved only once within Dipodium, on the Australian continent during the late Miocene–early Pliocene.
From the late Miocene–early Pliocene (ca. 5 Ma), climatic conditions in Australia became increasingly arid, leading to a decline of rainforest vegetation and expansion of open sclerophyllous forests (Quilty, 1994; Gallagher et al., 2003; Martin, 2006; He and Wang, 2021). By the end of the Pliocene, Australia’s landscape was similar to the present day, with much of the continent a mosaic of open woody vegetation dominated by Eucalyptus, Acacia, and Casuarinaceae (e.g., Martin, 2006). The Pleistocene (ca. 2.58–0.012 Ma) was characterised by climatic oscillations, which led to repeated forest expansion and contraction (Byrne et al., 2008). The evolution of mycoheterotrophy and the subsequent radiation of sect. Dipodium may have been facilitated by two factors: aridification in Australia favouring the reduction of leaf area to decrease water loss (O’Byrne, 2014) and the expansion of sclerophyll taxa and their mycorrhizal partners. Mycoheterotrophic Dipodium is assumed to share mycorrhizal fungi with Myrtaceae trees, especially Eucalyptus (Bougoure and Dearnaley, 2005; Dearnaley and Le Brocque, 2006; Jones, 2021), which explosively diversified and came to dominate most Australian forests and presumably led to increased diversity and abundance of suitable mycorrhizal partners for Dipodium. The rapid diversification of Dipodium from the Pleistocene onwards (ca. 3.2–0.3 Ma) ( Figure 4 ) may have been driven by cycles of population fragmentation and coalescence in response to climatic oscillations.
4.3. Plastid genome evolution
4.3.1. Plastome structural features and variations
In this study, whole plastome assemblies were generated for 24 Dipodium samples, including representatives of all leafless, putatively full mycoheterotrophs of sect. Dipodium found in Australia, one leafy photosynthetic species of sect. Dipodium (D. ensifolium), and one leafy photosynthetic species of sect. Leopardanthus (D. pandanum). The overall organisation and the plastid gene content are generally conserved in most examined Dipodium plastomes ( Figure 5 , Tables 2 , 3 ). All examined plastomes showed the typical quadripartite structure of angiosperms (Ruhlman and Jansen, 2014). However, some genomic features among several Dipodium plastomes were not conserved, including 1) differences in total genome length; 2) independent boundary shifts IRB/SSC/IRA within the plastome of D. pandanum 1, D. stenocheilum 1, and D. variegatum; 3) triplication of the trnV-GAC in the plastomes of D. ammolithum, D. elegantulum, D. hamiltonianum, D. stenocheilum 2, and D. interaneum; 4) the independent pseudogenisation of cemA in the plastome of D. aff. roseum 4 and trnD-GUC in the plastome of D. campanulatum 1; and 5) the pseudogenisation or loss to varying degrees of ndh genes ( Figure 5 , Table 3 ; Supplementary Material 7 ).
The total genome length of Dipodium plastomes displayed differences of approximately 10,000 bp between the smallest (142,949 bp; D. variegatum) and largest plastomes (152,956 bp, D. aff. roseum 3), which correlated with the level of ndh gene degradation. Some Dipodium plastomes were similar to the average size of orchid plastomes (152,442 bp) published on the NCBI database (286 Orchidaceae chloroplast genome, accessed on June 13, 2022; NCBI, 2022) however, most plastomes were smaller (average size Dipodium plastomes: 148,703 bp; Table 2 ). Average GC contents in Dipodium were very similar to the average GC content of published orchid plastomes on the NCBI database (NCBI, 2022) (ca. 36.8%; 286 Orchidaceae chloroplast genome, accessed on June 13, 2022), and all fell into the range of typical angiosperm plastomes (ca. 30%–40%) ( Table 2 ).
4.3.2. Patterns of ndh gene degradation within Dipodium
In orchids, ndh gene losses and pseudogenisations, which occurred in both autotrophic and heterotrophic species, have been documented in various genera (e.g., Kim et al., 2015; Feng et al., 2016; Niu et al., 2017; Barrett et al., 2018; Roma et al., 2018; Barrett et al., 2019; Lallemand et al., 2019; Kim et al., 2020; Peng et al., 2022; Kim et al., 2023). This study is in line with these general findings in that ndh gene degradation was also observed within the orchid genus Dipodium. All chloroplast ndh genes in Dipodium plastomes exhibited varying degrees of putative pseudogenisation and loss, and not a single ndh gene remained functional among the examined chloroplast genomes ( Table 3 , Figures 5 , 6 ). These findings include all plastomes of leafless putatively fully mycoheterotrophic species and two autotrophic leafy species (D. pandanum and D. ensifolium) and thus suggest that all examined species, independently of their nutritional status, have lost the functionality of the plastid NADH dehydrogenase complex. Hence, the last common ancestor of extant Dipodium is likely to have lacked a functional NDH complex. Previous studies in Cymbidiinae, the first diverging lineage in Cymbideae, found that all species studied so far exhibited at least one degraded ndh gene (e.g., Yang et al., 2013; Kim and Chase, 2017). As the next diverging lineage in Cymbidieae is Dipodium, this suggests that the degradation of ndh genes in Cymbidieae was likely a dynamic process from functional to non-functional. However, further research is needed, e.g., ancestral state reconstructions of gene degradation with increased taxonomic sampling. The inclusion of more species among sect. Leopardanthus is warranted to clarify if some ndh genes have remained functional in some autotrophic species of sect. Leopardanthus.
Previous studies examined ndh gene loss at the genus level and revealed an independent loss of function of the NADH dehydrogenase complex for several genera (e.g., Kim et al., 2015; Lin et al., 2015). However, comparative whole plastome studies examining gene degradation and loss among closely related mycoheterotrophic species are still scarce. For a better understanding of ndh gene degradation patterns, this study investigated the degree of ndh gene degradation among closely related orchid species ( Figure 6 ). The greatest degradation within Dipodium was found for ndhG, which is putatively lost in almost all examined plastomes, except D. stenocheilum 1, which retained a putative severely pseudogenised ndhG ( Figure 6 ). The ndhG gene is located within the SSC region. In general, it is well established that genes in the SSC region experience higher substitution rates compared to genes located within IR regions (Ruhlman and Jansen, 2014). The latter is the case for ndhB, which is located in the IRs and structurally more conserved in Dipodium compared to most ndh genes located in the SSC. The greatest degree of ndh gene degradation occurred in D. variegatum, which putatively lost ndhC and ndhE–ndhI. All other plastomes putatively lost at least one to three ndh genes and showed different levels of degradation ( Figure 6 ).
Interestingly, the level of ndh gene degradation varied even among closely related species within species complexes. For example, D. stenocheilum 1 independently lost ndhI and ndhF, whereas all other studied samples of the D. stenocheilum complex retained those two genes as moderately or severely pseudogenised ( Figure 6 ). Different levels of gene degradation and loss were even found within the same species. For example, D. atropurpureum 1 lost ndhC, whereas D. atropurpureum 2 retained a severely pseudogenised ndhC ( Figure 6 ). Moreover, the study of Kim et al. (2020) included one individual of D. roseum, which showed a different pattern of ndh gene loss and degradation to those found among the D. roseum samples of this study. D. roseum (MN200386) experienced complete loss of ndhA, ndhC–ndhI, and ndhK but retained pseudogenised ndhB and ndhJ genes (Kim et al., 2020). These findings also agree with the recent comparative plastome study on D. roseum and D. ensifolium: D. roseum (OQ885084) has retained truncated ndhB, ndhD, and ndhJ genes but completely lost ndhA, ndhC, ndhE–ndhI, and ndhK (McLay et al., 2023).
Overall, some patterns of ndh gene degradation found in this study in Dipodium are similar; however, many were unique for each individual examined. Hence, this suggests that sect. Dipodium has undergone a recent and active ndh gene degradation, which strongly implies a relaxed evolutionary selective pressure for the retention of the NDH complex.
4.3.3. IR/SSC junctions and IR instability
Orchidaceae plastomes frequently show an expansion/shift of the IR towards the SSC region (e.g., Kim et al., 2020). This instability of the IR/SSC junction is assumed to correlate with the deletion of ndhF and has resulted in a reduction of the SSC, as observed in several Orchidaceae plastomes (e.g., Kim et al., 2015; Niu et al., 2017; Dong et al., 2018; Roma et al., 2018) and other land plant plastomes (e.g., Amaryllidaceae, Bignoniaceae, and Orobanchaceae) (Thode and Lohmann, 2019; Könyves et al., 2021; Li et al., 2021). This study revealed reduced SSC regions for most examined plastomes, which correlated with the degradation of the ndh gene suite located in the SSC. Compared to typical SSC regions found in angiosperms (ca. 20 kb; Ruhlman and Jansen, 2014), the smallest SSC region was reduced by ca. 7,900 bp (D. variegatum), and the largest SSC region was reduced by ca. 4,700 bp (D. ensifolium) ( Table 2 , Figure 5 ). However, a large expansion of the IR such as found in Vanilla and Paphiopedilum plastomes (Kim et al., 2015) was not found in Dipodium (IR sizes ranging between 24,436 and 26,817 bp, Table 2 ).
In angiosperms, the ycf1 gene usually occupies ca. 1,000 bp in the IR (Kim et al., 2015; Sun et al., 2017). Dipodium plastomes in this study displayed varying positions of ycf1 within the IR. In plastomes in which the ndhF gene was completely lost or severely truncated, the portion of ycf1 within the IRA was mostly shorter compared to plastomes, which contained moderately truncated ndhF genes ( Figure 5 ). These results are similar to the findings of Kim et al. (2015), who compared the locations of the IR/single-copy region junctions among 37 orchid plastomes and closely related taxa in Asparagales. In at least three plastomes (D. pandanum 1, D. stenocheilum 1, and D. variegatum), ndhF was independently lost, and the SSC/IRB junction was shifted into the spacer region near the rpl32 gene in direct adjacency to the partially duplicated ycf1 fragment ( Figures 5B–D ). These findings suggest the deletion of ndhF correlated with the shift of the SSC/IRB junction. Interestingly, the boundaries between SSC and IR regions were found to be variable even among closely related species, e.g., in Cymbidium. Some species in Cymbidium showed similar patterns of IR/SSC shifts (Kim and Chase, 2017) as found in Dipodium.
In at least five plastomes (D. ammolithum, D. elegantulum, D. hamiltonianum, D. interaneum, and D. stenocheilum 2), the trnV-GAC gene was triplicated (i.e., duplicated trnV-GAC version in close proximity to each other in either IRA or IRB) ( Figures 5B, C , Table 3 ). To the best of our knowledge, similar tRNA duplication patterns within the IR regions have not yet been found in any other Orchidaceae plastomes. However, a recent study on plastomes of the angiosperm genus Medicago (Wu et al., 2021) yielded similar patterns. Wu et al. (2021) found three copies of the trnV-GAC gene in the plastomes of two closely related species within the IR (Medicago archiducis-nicolai and Medicago ruthenica), which were linked to forward and tandem repeats. Interestingly, the findings of Wu et al. (2021) support the hypothesis that repetitive sequences lead to genomic rearrangements and thus affect plastome stability. This may also apply to some Dipodium plastomes. However, to rule out any technical issues throughout the next-generation sequencing (NGS) process and to validate findings of duplicated tRNAs (and the above-mentioned boundaries of IR/SC regions), PCR amplification of affected regions should be carried out in future studies. However, in strong support of tRNA duplication is their independent presence within the IR of five plastomes among individuals of the same species complexes (D. stenocheilum complex and D. hamiltonianum complex). However, an increased sampling is necessary to better understand the impacts of genomic rearrangements due to repetitive sequences and thus plastome instability in Dipodium.
4.3.4. Evolution of mycoheterotrophy and associated plastome degradation in Dipodium
Heterotrophic plants are remarkable survivors, exhibiting often curious morphological, physical, or genomic modifications. Multiple heterotrophs were found to have suffered plastid genome degradations due to relaxed pressure on photosynthetic function. In recent years, evidence has accumulated that plastid genomes have undergone gene degradation in the evolutionary transition from autotrophy to heterotrophy (e.g., Wicke et al., 2016; Graham et al., 2017; Barrett et al., 2019). Among these, the first stage is the loss and pseudogenisation of genes involved in encoding the NDH complex. Interestingly, all examined plastomes of Dipodium have lost or pseudogenised all 11 ndh genes regardless of their nutritional status ( Figure 6 ). Two photosynthetic species with green leaves were included in this study, D. pandanum (sect. Leopardanthus) and D. ensifolium (sect. Dipodium). Degradation in ndh genes among photosynthetic species is not surprising and was frequently reported in previous plastome studies in land plants. The large-scale study on Orchidaceae plastomes of Kim et al. (2020) observed ndh gene pseudogenisation and losses among species in many epiphytes and several terrestrials that have retained their photosynthetic capacity. The NDH complex is thought to mediate the Photosystem I cyclic electron transport, fine-tune photosynthetic processes, and alleviate photooxidative stress (e.g., Yamori et al., 2015; Peltier et al., 2016; Sabater, 2021). D. pandanum is a terrestrial or climbing epiphytic orchid and highly localised in rainforest habitats, whereas the terrestrial D. ensifolium grows in open forests and woodlands (Jones, 2021); thus, both species seem to prefer shaded understory habitats. For epiphytic or terrestrial plants living in low-light habitats, it has been proposed that the NDH complex may not be essential anymore (e.g., Barrett et al., 2019). One reason for this may be that they are less exposed to photooxidative stress (e.g., Feng et al., 2016; Barrett et al., 2019). However, the NDH complex is composed of 11 chloroplast-encoded subunits and additional subunits encoded by the nucleus (e.g., Peltier et al., 2016). It has been established that genomic material was repeatedly exchanged between the nucleus, mitochondrion, and chloroplast in the evolutionary course of endosymbiosis. Thus, previous studies examined whether genes were transferred from the chloroplast to the nucleus and/or mitochondrion genome or whether nuclear genes for the NDH complex suffered under degradation. Indeed, Lin et al. (2015) reported ndh fragments within the mitochondrial genomes of orchids; however, no copies were found in the nuclear orchid genomes. Similar findings were reported from the orchid genus Cymbidium (Kim and Chase, 2017). However, further studies are needed to determine whether ndh gene transfer into the nucleus or mitochondrion may play a role within Dipodium.
The proposed subsequent next steps towards (myco-) heterotrophy is the functional loss of photosynthetic genes (e.g., psa, psb, pet, rbcL, or rpo) followed by genes for the chloroplast ATP synthase and genes with other functions such as housekeeping genes (e.g., matK, rpl, and rnn; e.g., Graham et al., 2017; Barrett et al., 2019). Most examined Dipodium plastomes displayed no additional plastid gene degradation in addition to ndh gene degradation, except in D. aff. roseum 4, where cemA was pseudogenised, and in D. campanulatum 1, where the trnD-GUC gene was pseudogenised ( Table 3 ). The cemA gene encodes the chloroplast envelope membrane protein and was found to be non-essential for photosynthesis; however, cemA-lacking mutants of the green alga Chlamydomonas were found to have a severely affected carbon uptake (Rolland et al., 1997) and may therefore be classified as directly involved in photosynthesis. Transfer RNA genes (trn) are involved in the translation process and categorised as “housekeeping” genes (e.g., Graham et al., 2017; Wicke and Naumann, 2018; Barrett et al., 2019). Moreover, similar gene degradation patterns were found in the plastomes of D. roseum (MN200386, Kim et al., 2020 and OQ885084, McLay et al., 2023) and D. ensifolium (OQ885084, McLay et al., 2023), which functionally lost all ndh genes. However, most photosynthesis-related genes in the plastomes of Dipodium were found to be functional. Thus, mycoheterotrophic species of Dipodium display evidence of being at the beginning of plastid gene degradation, in contrast with the majority of fully mycoheterotrophic orchids, which are in more advanced stages of degradation, e.g., Cyrtosia septentrionalis (Kim et al., 2019), Epipogium (Schelkunov et al., 2015), and Rhizanthella (Delannoy et al., 2011). In contrast, mycoheterotrophs such as Corallorhiza trifida (Barrett et al., 2018), Cymbidium macrorhizon (Kim et al., 2017), Hexalectris grandiflora (Barrett et al., 2019), and Limodorum abortivum (Lallemand et al., 2019) display functional losses within the plastid ndh genes only, and some species among them additionally lost one or two other genes, similar to findings in Dipodium. Interestingly, most of these species are leafless but considered putatively partially mycoheterotrophic. Suetsugu et al. (2018) demonstrated that the leafless green orchid C. macrorhizon contains chlorophyll and can fix significant quantities of carbon during the fruit and seed production phase and, thus, is photosynthetically active. Chlorophyll is present in C. trifida also, but this green, leafless coralroot is an inefficient photosynthesiser (Barrett et al., 2014). Some species among leafless orchids within sect. Dipodium (e.g., D. elegantulum, D. stenocheilum, and D. variegatum) appear green on stems ( Figure 1 , Jones, 2021), which suggests that they may contain some chlorophyll and be able to photosynthesise. Coupled with relatively mild plastid gene degradation compared to other fully mycohetrotrophic orchids, this suggests that some leafless species among sect. Dipodium may be partially mycoheterotrophic rather than fully mycoheterotrophic as has been hypothesised for D. roseum (Kim et al., 2020; McLay et al., 2023). However, no studies so far have examined whether leafless species among sect. Dipodium contain chlorophyll and whether they are capable of carrying out photosynthesis at sufficient rates. Therefore, more research is needed to assess the trophic status, including analysis of chlorophyll quantities and the ratio of photosynthetic carbon to fungal carbon for Dipodium.
Compared with recently published studies on mycoheterotrophic orchids such as Corallorhiza and Hexalectris (Barrett et al., 2018, 2019), which incorporated divergence-time estimations, plastomes of Dipodium showed the least degradation. Hexalectris crown age was estimated to be ca. 24 Ma, and plastomes of mycoheterotophs were more degraded compared to mycoheterotrophic plastomes of Corallorhiza, which diversified ca. 9 Ma onwards (Barrett et al., 2018, 2019). Dipodium diversified in the late Miocene ca. 11 Ma and the mycoheterotrophic lineage divergent from the autotrophic lineage ca. 8.1 Ma, which is slightly younger compared to Corallorhiza. Hence, time of divergence may play a role in the degree of degradation of Dipodium plastomes, which show an early stage of plastome degradation compared to older diverging mycoheterotrophic lineages that are in more advanced stages of plastome degradation.
5. Conclusion
This molecular phylogenomic comparative study clarified evolutionary relationships and divergence times of the genus Dipodium and provided support for two main lineages within Dipodium, corresponding to the morphologically defined sect. Dipodium and sect. Leopardanthus. A phylogenetic analysis resolved the leafy autotroph D. ensifolium as being part of sect. Dipodium and found to be in a sister group position to all leafless species in sect. Dipodium. Divergence-time estimations placed the divergence of the leafy species D. ensifolium from the remainder of section Dipodium in the late Miocene. Shortly after, the remaining clade including all leafless, putatively full mycoheterotrophic species within sect. Dipodium emerged ca. 7.3 Ma in the late Miocene followed by rapid species diversification from ca. 4.3 Ma onwards in the early Pliocene. Thus, this study indicates that mycoheterotrophy has most likely evolved only once on the Australian continent within Dipodium during the late Miocene and that the ancestors of putatively full mycoheterotrophic species may have had green leaves. Among the examined plastomes, all plastid ndh genes were pseudogenised or physically lost, regardless of the individual’s nutrition strategy (i.e., autotroph versus mycoheterotroph). Thus, this study provides molecular evidence of relaxed evolutionary selective pressure on the retention of the NADH dehydrogenase complex. Mycoheterotrophic species among sect. Dipodium retained a full set of other functional photosynthesis-related genes and exhibited an early stage of plastid genome degradation. Hence, leafless species of sect. Dipodium may potentially be rather partially mycoheterotrophic than fully mycoheterotrophic.
To further disentangle evolutionary relationships in Dipodium, future studies based on nuclear data such as those derived from target capture sequencing and with a denser sampling at the population level are warranted. Moreover, the inclusion of a denser sampling of sect. Leopardanthus is warranted to clarify if some ndh genes may have remained functional in some of the autotrophic species of sect. Leopardanthus. To obtain further insights into the nutritional strategies in Dipodium, future studies should assess the trophic status of mycoheterotrophic species in Dipodium based on physiological data such as from the analysis of chlorophyll quantities and the ratio of photosynthetic carbon to fungal carbon for Dipodium. The Australian orchid flora harbours many more remarkable mycoheterotrophic lineages (e.g., Danhatchia), which offer the opportunity to further explore the evolutionary pathways to mycoheterotrophy and associated plastid genome evolution. The inclusion of autotrophic plants into comprehensive plastid phylogenetic analyses could broaden the understanding of the significance of observed ndh gene degradation patterns within Orchidaceae.
Data availability statement
Sequence data presented in this study are deposited in the European Nucleotide Archive repository, project number PRJEB66849, accession numbers ERR12947508 to ERR12947535 and ERR12947593 to ERR12947597 (available at: https://www.ebi.ac.uk/ena/browser/view/PRJEB66849). Processed data files were deposited in the CSIRO Data Access Portal (https://doi.org/10.25919/6wcx-0h88) under the Creative Commons Attribution-License 4.0 Creative Commons Attribution 4.0 International Licence.
Author contributions
SG: Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Visualization, Writing – original draft, Writing – review & editing. MC: Conceptualization, Data curation, Funding acquisition, Investigation, Writing – review & editing. SB: Formal analysis, Investigation, Methodology, Writing – review & editing. JN: Investigation, Writing – review & editing. VP: Investigation, Writing – review & editing. DC: Funding acquisition, Writing – review & editing. PS: Investigation, Writing – review & editing. KN: Conceptualization, Data curation, Funding acquisition, Investigation, Methodology, Writing – review & editing.
Acknowledgments
The authors acknowledge the contribution of Bioplatforms Australia (enabled by NCRIS) in the generation of data used in this publication. They acknowledge K. Alcock, M.D. Barrett, C. Bower, C.P. Brock, R. Crane, D.M. Crayn, W. Dowling, J. Egan, B. Gray, C. Houston, M. Jacobs, D.L. Jones, P.D. Jones, C.D. Kilgour, L. Lawler, K.R. McDonald, I. Morris, D.E. Murfet, and J. Taylor s.n. for collection of plant material used in this study. A preprint of the manuscript was released online (Goedderz et al., 2024; DOI: doi.org/10.1101/2024.02.05.578113).
Funding Statement
The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This study was supported by the Australian Biological Resources Study (Dept. of Agriculture, Water and the Environment, Australian Government NTRGP BBR210–34) and the Australian Orchid Foundation (AOF325.18; AOF357.23). SG received a research grant from the Australian Tropical Herbarium.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpls.2024.1388537/full#supplementary-material
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
Sequence data presented in this study are deposited in the European Nucleotide Archive repository, project number PRJEB66849, accession numbers ERR12947508 to ERR12947535 and ERR12947593 to ERR12947597 (available at: https://www.ebi.ac.uk/ena/browser/view/PRJEB66849). Processed data files were deposited in the CSIRO Data Access Portal (https://doi.org/10.25919/6wcx-0h88) under the Creative Commons Attribution-License 4.0 Creative Commons Attribution 4.0 International Licence.