2024 Volume 65 Issue 3 Pages 138-150
The reproduction and dispersal strategies of lichens play a major role in shaping their population structure and photobiont diversity. Sexual reproduction, which is common, leads to high lichen genetic diversity and low photobiont selectivity. However, the lichen genus Endocarpon adopts a special co-dispersal model in which algal cells from the photobiont and ascospores from the mycobiont are released together into the environment. To explore the dispersal strategy impact on population structures, a total of 62 Endocarpon individuals and 12 related Verrucariaceae genera individuals, representing co-dispersal strategy and conventional independent dispersal mode were studied. Phylogenetic analysis revealed that Endocarpon, with a large-scale geographical distribution, showed an extremely high specificity of symbiotic associations with their photobiont. Furthermore, three types of group I intron at 1769 site have been found in most Endocarpon mycobionts, which showed a high variety of group I intron in the same insertion site even in the same species collected from one location. This study suggested that the ascospore-alga co-dispersal mode of Endocarpon resulted in this unusual mycobiont-photobiont relationship; also provided an evidence for the horizontal transfer of group I intron that may suggest the origin of the complexity and diversity of lichen symbiotic associations.
Lichens are defined as highly specific mutualistic symbiotic associations between lichen-forming fungi (the mycobiont) and their algal partners (the photobiont, usually green algae and/or cyanobacteria) (Nash, 2008). The patterns of association between the mycobionts and photobionts are described by the degree of specificity, i.e. the phylogenetic range of associated partners, and of selectivity, i.e. the frequency of association among partners (Yahr et al., 2004). There are varying degrees of specificity for photobionts to maintain the co-evolution of lichen symbioses. While some mycobiont species can associate with a wide range of photobiont species, showcasing algal diversity, different fungal species may share the same algal partner, allowing for the possibility of algal partners switching among different lichen-forming fungi across different species, genera, and families (Ahmadjian & Jacobs, 1987; Beck et al., 1998; Hauck et al., 2007; Hawksworth, 1988). Various factors may influence the selectivity and specificity of lichen-forming fungi and their photobionts, including stress and extreme environmental conditions, which have been found to reduce photobiont selectivity in both green algae and cyanobacteria (Vargas Castillo & Beck, 2012; Wirtz et al., 2003).
Reproductive and dispersal strategies play significant roles in shaping photobiont diversity and population structure in lichens (Otalora et al., 2013; Steinova et al., 2019). Lichen reproduction occurs through sexual, asexual, or vegetative means (Frohlich, 2003). The sexual reproduction structure of ascomycete lichens takes place in a structure called ascomata, which is divided into four types based on its morphological structure: apothecia, perithecia, locules, and patsches (some lichens lack a true ascomata). In nature, most lichen-forming fungi reproduce sexually by producing meiospores that are dispersed independently into the environment, where they must find compatible photobiont cells to re-establish symbiosis under challenging conditions. This process carries a high risk of failure due to the limitations of timing and partner compatibility, although some lichenized fungi have been shown to temporarily associate with non-preferred partners or exist in a free-living state to prolong their survival time (Etges & Ott, 2001; O'Brien et al., 2013). On the other hand, vegetative reproduction does not face the same restrictions, as cloning does not depend on encountering symbiotic algae in the environment. However, this type of reproduction has its own limitations, with clonal propagules being limited to short dispersal distances, unlike sexual reproduction which can facilitate long-distance dispersal (Ronnas et al., 2017; Scheidegger & Werth, 2009; Walser, 2004).
Previous studies revealed that lichen-forming fungi that use sexual reproduction strategies tend to have low selectivity for photobionts, and lichen-forming fungi with low photobiont selectivity demonstrated stronger adaptability to different ecological niches, enabling them to establish symbiotic relationships in a wide range of habitats (Muggia et al., 2014). In the order Verrucariales, vegetative reproduction through structures such as soredia, isidia, or blastidia is very rare (Geiser et al., 2006). Endocarpon Hedw. (Verrucariaceae, Verrucariales, Ascomycota) is a famous genus in this order that has a unique co-dispersal mode of reproduction. Its perithecium contains both ascospores and hymenial algal cells, and both partners are released together into the environment during spore maturation (Geitler, 1938; Shukla et al., 2014). This differs from other sexually reproducing lichen species. The sexual reproductive structures of Endocarpon are critical to this co-dispersal strategy and appear to facilitate successful lichenization in various ecological conditions, although this possibility has not yet been reported. To investigate the photobiont selectivity in this co-dispersal strategy of Endocarpon and how this strategy shapes lichen population structures, we collected a large number of thalli from Endocarpon and three closely related genera with different dispersal modes: Placidiopsis Beltr., Placidium A. Massal., and Verrucaria Schrad. The samples were collected on a large geographical scale across China, and we explored the dispersal mode and performed phylogenetic analysis of the mycobionts and photobionts to address these questions.
A total of 74 individuals were collected from six geographic regions that spanned a distance of over 2000 km, all within China (Fig. 1). Among the individuals, 62 Endocarpon were collected from Diqing in Yunnan province, Guoluo in Qinghai province, Helan Mountain in Ningxia Hui Autonomous Region, Linzhi in Tibet Autonomous Region and Yanchi in Ningxia Hui Autonomous Region. Twelve other individuals belonged to three related genera: Verrucaria, Placidiopsis, and Placidium. Three were Placidiopsis sampled from Helan Mountain, four were Verrucaria from Diqing and Helan Mountain, and five were Placidium from Linzhi and Duolun. The information of all the specimens in this study is listed Table 1.
No. | No. of thallus | Species name | Locality | GenBank no. | Group I Intron (site 1769) | ||
No. of lichen-forming fungi | No. of photobionts | Length (bps) | Type | ||||
1 | HL12Y023 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361512 | OQ361402 | 235 | Short |
2 | HL12Y033-1 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361513 | OQ361406 | 235 | Short |
3 | HL12Y033-2 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361514 | OQ361407 | 235 | Short |
4 | HL12Y045 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361515 | OQ361408 | 234 | Short |
5 | HL12Y071 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361517 | OQ361411 | 235 | Short |
6 | HL12Y073 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361518 | OQ361412 | 235 | Short |
7 | HL12Y078 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361520 | OQ361415 | 235 | Short |
8 | HL12Y134 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361524 | OQ361426 | 235 | Short |
9 | HL12Y187 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361528 | OQ361439 | 236 | Short |
10 | HL12Y215 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361535 | OQ361450 | 235 | Short |
11 | HL12Y216 | Endocarpon adsurgens | Helan Mountain, Ningxia, China | OQ361536 | OQ361451 | 235 | Short |
12 | YC12Y015 | Endocarpon adsurgens | Yanchi, Ningxia, China | OQ361511 | OQ361399 | 237 | Short |
13 | YC12Y131 | Endocarpon adsurgens | Yanchi, Ningxia, China | OQ361523 | OQ361425 | 237 | Short |
14 | DQ12Y003 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361509 | OQ361393 | 228 | Short |
15 | DQ12Y010 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361510 | OQ361396 | 234 | Short |
16 | DQ12Y066 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361516 | OQ361409 | 235 | Short |
17 | DQ12Y076 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361519 | OQ361414 | - | - |
18 | ZD12Y091 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361521 | OQ361421 | 235 | Short |
19 | ZD12Y095 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361522 | OQ361422 | 235 | Short |
20 | ZD12Y173 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361525 | OQ361434 | 234 | Short |
21 | ZD12Y178 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361526 | OQ361437 | 235 | Short |
22 | ZD12Y185 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361527 | OQ361438 | 222 | Short |
23 | ZD12Y187 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361529 | OQ361440 | 234 | Short |
24 | ZD12Y188 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361530 | OQ361441 | 234 | Short |
25 | ZD12Y189 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361531 | OQ361442 | 234 | Short |
26 | ZD12Y192 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361532 | OQ361443 | 234 | Short |
27 | ZD12Y193 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361533 | OQ361444 | 234 | Short |
28 | ZD12Y201 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361534 | OQ361448 | 234 | Short |
29 | ZD12Y223 | Endocarpon adsurgens | Diqing, Yunnan, China | OQ361537 | OQ361453 | 234 | Short |
30 | XZ12Y366 | Endocarpon adsurgens | Linzhi, Tibet, China | OQ361538 | OQ361456 | 234 | Short |
31 | XZ12Y409 | Endocarpon adsurgens | Linzhi, Tibet, China | OQ361539 | OQ361457 | - | - |
32 | XZ12Y424 | Endocarpon adsurgens | Linzhi, Tibet, China | OQ361540 | OQ361459 | - | - |
33 | HL12Y013 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361470 | OQ361397 | 235 | Short |
34 | HL12Y014 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361471 | OQ361398 | 366 | Long |
35 | HL12Y017 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361472 | OQ361400 | 488 | Long |
36 | HL12Y019 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361473 | OQ361401 | 338 | Long |
37 | HL12Y028 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361474 | OQ361404 | 235 | Short |
38 | HL12Y029 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361475 | OQ361405 | 251 | Medium |
39 | HL12Y076 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361476 | OQ361413 | 234 | Short |
40 | HL12Y083 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361477 | OQ361416 | 253 | Medium |
41 | HL12Y085 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361478 | OQ361417 | 253 | Medium |
42 | HL12Y089 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361479 | OQ361419 | 251 | Medium |
43 | HL12Y118-1 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361480 | OQ361423 | 502 | Long |
44 | HL12Y120 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361481 | OQ361424 | 231 | Short |
45 | HL12Y147 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361483 | OQ361428 | 235 | Short |
46 | HL12Y213 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361486 | OQ361449 | - | - |
47 | HL12Y227 | Endocarpon pusillum | Helan Mountain, Ningxia, China | OQ361487 | OQ361454 | 235 | Short |
48 | YC12Y146 | Endocarpon pusillum | Yanchi, Ningxia, China | OQ361482 | OQ361427 | 233 | Short |
49 | YC12Y155 | Endocarpon pusillum | Yanchi, Ningxia, China | OQ361484 | OQ361430 | 233 | Short |
50 | ZD12Y176 | Endocarpon pusillum | Diqing, Yunnan, China | OQ361485 | OQ361435 | 252 | Medium |
51 | YC12Y153 | Endocarpon. deserticola | Yanchi, Ningxia, China | OQ361488 | OQ361429 | 392 | Long |
52 | YC12Y157 | Endocarpon. deserticola | Yanchi, Ningxia, China | OQ361489 | OQ361431 | 529 | Long |
53 | HL12Y222 | Endocarpon. nigromarginatum | Helan Mountain, Ningxia, China | OQ361469 | OQ361452 | 232 | Short |
54 | Q11Y198 | Endocarpon. nigromarginatum | Guoluo, Qinghai, China | OQ361467 | OQ361445 | 231 | Short |
55 | Q11Y200 | Endocarpon. nigromarginatum | Guoluo, Qinghai, China | OQ361468 | OQ361447 | 232 | Short |
56 | HL12Y087 | Endocarpon. petrolepideum | Helan Mountain, Ningxia, China | OQ361502 | OQ361418 | 237 | Short |
57 | Q11Y269 | Endocarpon. petrolepideum | Guoluo, Qinghai, China | OQ361503 | OQ361455 | 221 | Short |
58 | HL12Y067 | Endocarpon. sinense | Helan Mountain, Ningxia, China | OQ361504 | OQ361410 | 240 | Short |
59 | HL12Y091 | Endocarpon. sinense | Helan Mountain, Ningxia, China | OQ361505 | OQ361420 | 232 | Short |
60 | YC12Y159 | Endocarpon. sinense | Yanchi, Ningxia, China | OQ361506 | OQ361432 | 233 | Short |
61 | ZD12Y177 | Endocarpon. unifoliatum | Diqing, Yunnan, China | OQ361507 | OQ361436 | 234 | Short |
62 | YC12Y026 | Endocarpon sp. | Yanchi, Ningxia, China | OQ361508 | OQ361403 | 235 | Short |
63 | HL12Y046 | Placidiopsis sp. | Helan Mountain, Ningxia, China | OQ361490 | OQ361460 | - | - |
64 | HL12Y166 | Placidiopsis sp. | Helan Mountain, Ningxia, China | OQ361491 | OQ361461 | - | - |
65 | HL12Y172 | Placidiopsis sp. | Helan Mountain, Ningxia, China | OQ361492 | OQ361463 | - | - |
66 | XZ12Y360 | Placidium sp. | Linzhi, Tibet, China | OQ361494 | OQ361466 | - | - |
67 | XZ12Y411 | Placidium sp. | Linzhi, Tibet, China | OQ361495 | OQ361458 | - | - |
68 | DL12Y004 | Placidium sp. | Duolun, Inner Mongolia, China | OQ361496 | OQ361394 | - | - |
69 | DL12Y008 | Placidium sp. | Duolun, Inner Mongolia, China | OQ361497 | OQ361395 | - | - |
70 | DL12Y030 | Placidium sp. | Duolun, Inner Mongolia, China | OQ361493 | OQ361465 | - | - |
71 | HL12Y169 | Verrucaria sp. | Helan Mountain, Ningxia, China | OQ361499 | OQ361462 | - | - |
72 | ZD12Y168 | Verrucaria sp. | Diqing, Yunnan, China | OQ361498 | OQ361433 | - | - |
73 | ZD12Y196 | Verrucaria sp. | Diqing, Yunnan, China | OQ361500 | OQ361464 | - | - |
74 | ZD12Y199 | Verrucaria sp. | Diqing, Yunnan, China | OQ361501 | OQ361446 | - | - |
Note: “-” means that no group I introns can be found at 1769 site in mycobionts, which does not mean that mycobionts do not contain other group I introns.
Total DNA from mycobionts and photobionts was extracted using a modified CTAB method (Zhou et al., 2006). The mycobiont ITS segments were then amplified using the fungal specific primer pairs ITS5 (5’-TCCTCCGCTTATTGATATGC-3’) and ITS4 (5’-GGAAGTAAAAGTCGTAACAAGG-3’) (White et al., 1990).
For the photobiont ITS sequences, algal-specific primer pairs nr-SSU-1780-5’ (5’-CTGCGGAAGGATCATTGATTC-3’) and nr-LSU-0012-3’ (5’-AGTTCAGCGGGTGGTCTTG-3’) were used (Piercey-Normore & DePriest, 2001). The PCR reaction was performed as follows: initial denaturation at 95 °C for 5 min, followed by 35 amplification cycles of 95 °C for 30 s, 53 °C for 45 s, 72 °C for 1 min, and a final extension at 72 °C for 5 min.
Then, dideoxy-mediated chain-termination sequencing reaction electrophoresis was conducted using the 3730XL DNA Sequencing Instrument (Applied Biosystems, CA, USA). The sequencing primers were the same as those described for PCR. Double-directional sequence data were obtained for the mycobionts and photobionts. These data were checked and assembled using the SEQMAN program within the Lasergene v7.1 software package (DNAStar Inc.,WI, USA).
2.3. Data analysis and phylogenetic tree constructionAll sequences generated in this study have been submitted to NCBI, and their accession numbers are listed in Table 1. We checked the sequence length of all data and found that the large variation in sequence length (582-1066 bps) of lichenized fungi indicated the presence of group I intron. To determine the insertion sites of these introns, we retrieved the 18S rRNA gene sequence of Saccharomyces cerevisiae (Desm.) Meyen (GenBank no. Z75578) and the 16S rRNA sequence of Escherichia coli (Migula) Castellani and Chalmers from GenBank, and aligned these sequences with our data.
The sequences analyzed in this study were divided into three datasets: the mycobiont ITS dataset, the group I intron dataset, and the photobiont ITS dataset. The group I introns, small subunit region (SSU) and large subunit (LSU) rDNA have been removed from the mycobiont matrix before undertaking the phylogenetic analysis (Supplementary Fig. 1). For the mycobiont and the photobiont ITS datasets, preliminary alignment was performed using the ClustalW algorithm included in MEGA11 software (Tamura et al., 2021). In the alignment of group I introns from mycobionts, the secondary structures were constructed prior to performing the alignment and the alignment was conducted using ClustalW embedded in MEGA with default parameters (Tamura et al., 2021; Thompson et al., 1994) and then made manual adjustments to ensure that the conserved elements remained properly aligned within the sequences. Alignment gaps were treated as missing data. The phylogenetic trees for the mycobionts, photobionts, and group I introns were constructed using the minimum evolution (ME) method with MEGA11. The Kimura two-parameter model was used to estimate the number of nucleotide substitutions. Pairwise deletion was used for the gaps and missing data treatment, while default settings were used for other parameters. The support values for the phylogenies were assessed with 1000 bootstrap replicates.
2.4. Group I intron secondary structure predictionWe used DNAMAN software V9.0 (Lynnon Biosoft, Quebec, Canada) to convert the group I introns into RNA sequences. Subsequently, thermodynamically stable structures were calculated using RNAStructure 3.5 (Mathews et al., 1999). Finally, the secondary structures of the group I introns were prepared using Adobe Illustrator 2021 (Adobe Systems Inc., CA, USA).
The ME tree of mycobiont based on the ITS rDNA sequences exhibit four distinct monophyletic groups: Endocarpon, Verrucaria, Placidiopsis, and Placidium (Fig. 2). The Endocarpon, Placidiopsis, and Placidium groups are powerfully supported with a 99% bootstrap value. The Verrucaria group exhibits slightly less support, with a 63% bootstrap value.
In this study, phylogenetic analyses were conducted on 62 Endocarpon individuals, with 61 of them being identified as belonging to seven species. These species manifest as follows: E. adsurgens Vain., E. deserticola T. Zhang, X.L. Wei and J.C. Wei, E. unifoliatum T. Zhang, X.L. Wei and J.C. Wei, E. petrolepideum (Nyl.) Hasse, E. nigromarginatum H. Harada, E. sinense H. Magn., and E. pusillum Hedwig. The remaining individual was marked as Endocarpon sp. which was considered to be an unidentified lineage or unreported species. Out of these species, E. adsurgens is monophyletic and comprises 32 individuals collected from various locations including Helan Mountain in Ningxia, Yanchi in Ningxia, Linzhi in Tibet, and Diqing in Yunnan. This species can be further divided into several sub-groups; however, most of these sub-groups lack strong support. There is no clear association between the clustering of individuals and their geographic origins, although some individuals collected from the same location did show a tendency to cluster together.
Phylogenetic analysis shows that E. pusillum forms a well-supported monophyletic group with 98% bootstrap support, consisting of 18 individuals collected from three locations: 15 from Helan Mountain, two from Yanchi, and one from Diqing. The E. pusillum group can be further divided into three distinct monophyletic sub-groups. The first sub-group comprises individuals from Helan Mountain and is supported by 68% bootstrap, while the second sub-group includes individuals from Helan Mountain and Yanchi that are geographically close (separated by dozens of kilometers) and has a high bootstrap support of 99%. The third sub-group is composed of individuals from Helan Mountain and Diqing, which are located about 1300 km apart, and has a bootstrap support of 60%. The E. pusillum individuals collected from Helan Mountain are assigned to the three sub-groups described above, indicating that the species is polyphyletic in this geographic area. Furthermore, similar to E. adsurgens, the clustering of E. pusillum is not strictly based on collection location. Among the other Endocarpon species, E. deserticola, E. unifoliatum, E. petrolepideum, E. nigromarginatum, and E. sinense groups consist of fewer individuals, but each group is monophyletic.
The ME tree of the mycobiont shows that individuals sharing identical ITS genotypes were likely to originate from the same habitat. We have found evidence across different species; for example, HL12Y028F E. pusillum and HL12Y147F E. pusillum, HL12Y078F E. adsurgens and HL12Y216F E. adsurgens, Q11Y198F E. nigromarginatum and Q11Y200F E. nigromarginatum. Additionally, in many other branches, individuals tend to cluster with other individuals from the same or nearby locations.
3.2. Phylogenetic analyses of photobiont ITS rDNAIn the present study, we obtained 74 ITS rDNA sequences of photobionts and conducted molecular analysis by constructing ME tree. The analyses demonstrated that the majority of the photosynthetic partners were classified into two well-supported monophyletic groups with high bootstrap support (99%). These two groups were recognized as distinguishable taxa at the species level, namely the Diplosphaera chodatii Bialosuknia and Stichococcus mirabilis Lagerheim (Fig. 3).
Sixty-seven individuals constituted the Diplosphaera chodatii group, of which 62 individuals of Endocarpon were collected from Helan Mountain, Yanchi in Ningxia, Linzhi in Tibet, and Diqing in Yunnan, two individuals of Verrucaria were collected from Diqing in Yunnan, and three individuals of Placidium were collected from Linzhi in Tibet and Duolun in Inner Mongolia, which suggests that the distribution of D. chodatii occurred across a large geographical range. Furthermore, D. chodatii exhibited low genetic diversity according to the phylogenetic analysis. No evidence was found that the genotypes of photobionts were related to geographical locations or even the host mycobiont species.
Both the Verrucaria and Placidium genera exhibited photobiont diversity. For example, Verrucaria from Diqing form associations with two algal partners, namely the green algae D. chodatii and S. mirabilis. Placidium from Linzhi and Duolun harbored D. chodatii and Pseudochlorella spp. as their photosynthetic partners. Although the data showed that three photobiont individuals from Placidiopsis sampled from Helan Mountain were identified as S. mirabilis, a previous study indicated that it could also form lichen symbiosis with D. chodatii (Thüs et al., 2011). Mycobionts from all species of Endocarpon collected in different locations exhibited high selectivity toward D. chodatii, which was also shared with other genera of lichenized fungi in the same habitat. This finding suggest the existence of algal pools in these habitats.
3.3. Group I intron analysesThrough sequence alignment, it was found that 58 out of 62 Endocarpon individuals harbor a group I intron (Table 1; Fig. 2). The insertion site was calibrated at 1769 based on the SSU rDNA sequence of S. cerevisiae (GenBank no. Z75578) as reference (Cao et al., 2011), and this site is 1506 based on the SSU rDNA sequence of E. coli (Bhattacharya et al., 2002; Del Campo et al., 2009; Friedl et al., 2000; Nyati et al., 2013).The group I introns were classified into three groups based on their lengths (Gutierrez et al., 2007), which are marked as the “short 1769 group” (221-240 bps), the “medium 1769 group” (251-253 bps), and the “long 1769 group” (338-529 bps), as shown in Table 1. The ME tree of group I introns shows three well-supported clades (Fig. 4). Clade I contains 47 introns from E. pusillum, E. adsurgens, E. unifoliatum, E. petrolepideum, E. nigromarginatum, E. sinense, and Endocarpon sp., while Clade II contains six introns, all from E. pusillum, and Clade III is composed of five introns from E. deserticola and E. pusillum. The group I introns in Clade I all belongs to the short 1769 group and form monophyletic sub-clades according to their host mycobiont species. In addition, similar to the analysis in photobionts and mycobionts, the introns do not show a correlation between intron genotypes and geographical locations. Five out of six introns in Clade II belong to the medium 1769 group, which form a separate sub-clade with 71% support, while the final intron belonged to the long 1769 group, and introns in Clade III all belong to the long 1769 group. It is particularly striking that the group I introns from E. pusillum collected in Helan Mountain are polyphyletic, and the short, medium, long, and non-intron types can all be found in E. pusillum from Helan Mountain.
Previous analyses show that the secondary structure of group I introns from the same insertion site is conserved, and most of the conserved nucleotides are located in the elements P, Q, R, and S (Burke et al., 1987; Del Campo et al., 2009). Group I introns generally have base pairing regions named P1 to P9, and the P4 region is formed by P and Q, while the P7 region consists of R and S. However, in this study these elements are not completely consistent in the three clades, as shown in Table 2 and Figure 5. The P7 element is the most conserved, while P3 and P4 showed high similarity in the medium and long groups, but not in the short group. The results show that introns from the short 1769 group harbor a larger P6 (Fig. 5A). Figure 5B illustrates the secondary structure of the medium 1769 group, whose P8 elements are similar to those in the short 1769 group in length but the sequence in P3/P4 elements are similar to those in the long 1769 group. In addition, the long 1769 group has a particularly large P8 region, but some members of this group lack the P5 element (Fig. 5C-E). Among the long group, the intron from HL12Y014F is rather special because sequences of its P3-P6 elements are identical with those from the medium group (Fig. 5C).
P3 | P4 P | P4' Q | P7 R | P3' | P7' S | |
Clade I | TAACCA | GCGTC | GACGT | CAGATTA | TGGTGG | TAATCG |
Clade II | CGTCACT | TGCTGG | TCAGCA | CAGATTA | AGTGACG | TAATCG |
Clade III | CGTCACT | CTGCTGG | CCAGCAG | CAGATTA | GGTGACG | TAATCG |
The ribosome ITS rDNA is a critical tool in lichen research for investigating phylogenetic relationships and species diversity in fungi and green algae at both the interspecific and intraspecific levels (Begerow et al., 2010; Moniz & Kaczmarska, 2010; Schoch et al., 2012). The ITS region is a crucial DNA barcode for species identification, evolutionary relationship analysis, and fungal diversity research in mycology. Phylogenetic analysis based on ITS markers has revealed the evolutionary relationship among closely related species of Rhizoplaca Zopf in China (Dal-Forno et al., 2016; Zhou et al., 2006). In the study of algae, the ITS rDNA marker is also used to reveal the diversity of algae and their environmental adaptability. For example, the photobiont diversity of Dermatocarpon, a member of Verrucariaceae, was analyzed using the ITS rDNA marker, which showed that mycobionts in different habitats exhibited the ability to capture the same photobiont (Fontaine et al., 2012). The ITS rDNA marker is also applicable in studying the relationship between mycobionts and photobionts in lichen symbiosis. In a previous study, the ITS rDNA-barcode was used to assess the degree of photobiont selectivity and specificity in thalli from multiple genera, including Carbonea Hertel, Austrolecia Hertel, Lecanora Ach., Lecidella Körb., Caloplaca Th. Fr., Umbilicaria Hoffm., collected from extreme ecosystems in Antarctica (Perez-Ortega et al., 2012). In this present study, ITS rDNA was used to reveal the relationships between Endocarpon and three closely related genera and their photobionts. The study demonstrates the ability of the ITS rDNA marker to distinguish different species or approximate genera in both lichenized fungi and their photosynthetic partners. Thus, the findings of this study suggest that ITS rDNA, as a classical marker, still plays an essential role in revealing the ascospore-alga co-dispersal mode of Endocarpon.
4.1. Unusual population structures shaped by co-dispersal strategy in EndocarponThe relationship pattern between mycobionts and their photobionts is one of the core research hotspot of lichen biology, and is influenced by the specificity and selectivity of mycobionts toward their photosynthetic partners. Numerous studies on photobiont selectivity reveal the complexity of symbiotic relationships, with research focusing on species differentiation, environmental factors, reproductive strategies, and dispersal modes. For instance, researchers have conducted studies on photobiont selectivity, exploring the topic from different perspectives (De Carolis et al., 2022; Hauck et al., 2007; Merinero et al., 2017; Muggia et al., 2014; Steinova et al., 2019; Vargas Castillo & Beck, 2012). In our previous study on two green-algae-harboring lichens from Umbilicaria esculenta (Miyoshi) Minks and U. muehlenbergii (Ach.) Tuck., which used different reproductive strategies, it was found that species using sexual reproduction exhibited low levels of photobiont selectivity compared to that using a vegetative reproduction strategy (Cao et al., 2015). A similar study on other green-algae-harboring lichen Cladonia P. Browne, also obtained a consistent conclusion (Steinova et al., 2019). Likewise, a study on the cyanobacteria-harboring-lichen Degelia Arv. and D.J. Galloway also showed that sexual species exhibited higher genetic diversity than asexual species, and asexual species formed high-specificity relationships with cyanobionts (Otalora et al., 2013). These findings suggest that photobiont selectivity is low in lichens with the strategy of sexual reproduction in the mycobiont because fungal spores must capture a variety of photobionts to stabilize the symbiotic association, or the mycobiont will not survive.
The present research investigated 62 individuals of Endocarpon that were collected from six regions in China, with a distance range between collection sites of 100-2000 km (Fig. 1; Table 1). The ME tree of mycobiont based on the ITS rDNA sequences revealed that these individuals could be divided into seven independent species with high support, and there was no difference in algae selectivity among species. The study further revealed that Endocarpon, a genus that strictly relies on sexual reproduction, exhibited an unusual mycobiont-photobiont selectivity pattern, which was contrary to the results of previous studies on lichens whose mycobionts used sexual reproduction. By contrast, individuals from the other three genera; Verrucaria, Placidiopsis, and Placidium, which are also in Verrucariaceae, showed low photobiont selectivity.
Endocarpon showed extremely high specificity for their photosynthetic partners, with all thalli from different species in Endocarpon establishing symbiotic relationships with only one green alga, D. chodatii, as shown in Figure 3. Hence, this close association between Endocarpon fungi and the green alga D. chodatii was fixed before the divergence of Endocarpon, and the present distribution pattern was shaped under long-term co-evolution and environmental adaptation.
The constructed ME trees of mycobiont and photobiont, based on the ITS rDNA sequences, indicate that neither mycobionts nor photobionts were divided according to geographical locations. The lack of distance isolation suggests that there is frequent gene flow or dispersal across a wide range of environments. During the development of lichen, the photobionts associated with mycobionts can change, a process called algae switching or photobiont switching (Piercey-Normore & DePriest, 2001). In some lichenized fungi, photobiont switching can lead to changes in morphology and reproduction strategies (Ertz et al., 2018). The phylogeny obtained in this study revealed that, in addition to Endocarpon, the genera Verrucaria and Placidium in the same habitat also selected D. chodatii to establish symbiotic relationships. However, D. chodatii were not divided into different lineages according to the different genera of host lichens or geographical regions (Fig. 3). This lichen family, Verrucariaceae, is characterized by a different trend in photobiont diversity and often forms associations with Stichococcus-like green algae, but the predominant photobionts Trebouxia Puymaly and Asterochloris Tschermak-Woess in most other lichens are only rarely or are never reported. In this family, Diplosphaera, Stichococcus Naegeli, and Protococcus C. Agardh are the most common lichen photobionts, and D. chodatii is shared among multiple mycobionts (Thüs et al., 2011). The present study suggests that there is an algal pool of D. chodatii in the sampled habitats. Considering the highly specific relationship between Endocarpon and D. chodatii we speculate that algae switching or photobiont stealing may occur in non-Endocarpon species because the unique co-dispersal mechanism of Endocarpon can provide abundant compatible algae in the habitat. The individuals from the other three genera in this study may establish an association with D. chodatii through re-lichenization or trans-lichenization, as described in a recent review (Pichler et al., 2023). Overall, the results suggest that there is a complex relationship between lichenized fungi and their photobionts, with frequent gene flow or dispersal of photobionts across a wide range of environments, and potential mechanisms of algae switching or photobiont stealing in non-Endocarpon species.
This high level of photobiont selectivity at the genus level is exceptionally rare among sexually reproducing lichens in nature. Typically, spores are dispersed independently, and it is necessary to find compatible algae cells in the habitat for successful lichenization to occur (Macedo et al., 2009). During this period, it can be challenging for fungi to find their compatible algal partners. Even if they do encounter them by chance, re-lichenization can take several stages to succeed. This is why sexual reproduction is often accompanied by low photobiont selectivity, which increases ecological tolerance, and improves the chances of successful symbiosis between widely distributed fungi and locally available photobionts (Muggia et al., 2014).
However, as a genus that relies on sexual reproduction, Endocarpon adopts a special co-dispersal model in which algal cells from the photobiont and ascospores from the mycobiont are sprayed into the habitat at the same time, which may explain the special relationship between Endocarpon and D. chodatii. This co-dispersal strategy seems to be more convenient for re-lichenization compared to single-dispersal sexually reproductive species. Moreover, chemical communication between mycobionts and photobionts plays an essential role from the early stages of lichenization up to the formation of thalli (Pichler et al., 2023). Therefore, for Endocarpon ascospores, there are compatible and identifiable symbiotic partners in the habitat, creating extremely favorable conditions for re-lichenization. This relationship may have been strengthened during evolutionary history of Endocarpon. Overall, the high photobiont selectivity of Endocarpon at the genus level is a fascinating finding that challenges our understanding of lichen evolution and adaptation.
In previous studies, co-dispersal in lichens was reported to occur mainly through vegetative reproduction, which is limited to short distances due to low evolutionary flexibility and selective specialization (Dal Grande et al., 2012; Ronnas et al., 2017; Steinova et al., 2019). However, the use of ascospores for dispersal in Endocarpon has allowed for long-distance transmission, providing a significant ecological advantage over lichens that rely on vegetative reproduction. This advantage is reflected in the widespread distribution of Endocarpon species across different regions and environments worldwide since they have been reported in many countries and regions ranging from terrestrial to marine and fresh water environments to arid environments, especially in biological soil crusts (Gueidan et al., 2007; Mead & Gueidan, 2020). Moreover, some Endocarpon species, such as E. pusillum, exhibit strong drought tolerance and both bionts in the symbiotic association play an important role in adaptation to harsh environmental conditions (Medwed et al., 2021; Wang et al., 2014). The special co-dispersal mode of the mycobiont and photobiont in Endocarpon may also improve its stress tolerance, expanding its ability to survive and thrive in a wider range of environments. In general, the findings of this study suggest that Endocarpon has advantage on long-distance transmission of sexual reproduction and avoids the disadvantages in re-lichenization through the use of a special co-dispersal strategy. Furthermore, this co-dispersal strategy likely contributes to the adaptability and success of Endocarpon in diverse ecological niches. Endocarpon was the first lichen whose genome was sequenced(Wang et al., 2014), and recently, the genome of the photobiont D. chodatii has also been made available online (Gueidan et al., 2023). This will greatly facilitate research into this co-dispersal strategy of Endocarpon. In future studies, we can anticipate using a wider range of tools and methods to explore the symbiotic relationship between Endocarpon and D. chodatii.
4.2. Evolutionary history reflected by group I introns in EndocarponGroup I introns were first discovered in the LSU of Tetrahymena thermophilia Nanney and McCoy by Cech et al. (1981). Since then, numerous studies have shown that group I introns are widely distributed among diverse organisms, including protists, plants, eubacteria, archaea, and even lichenized fungi and photobionts (Bhattacharya et al., 2000; Del Hoyo et al., 2018; Depriest & Been, 1992; Gargas et al., 1995; Nawrocki et al., 2018). The splicing site of group I introns is characterized by the conservative nucleotide 5’-U↓… …G↓ 3’, and its secondary structure is more conservative compared to the primary structure. Studies have shown that group I introns are divided into three domains: the P1-P2 domain, P4-P6 domain, and P3-P9 domain (including P3, P7, P8, and P9), of which the latter two constitute the catalytic center of the intron ribozyme. As mobile genetic elements, group I introns have the characteristics of frequent loss and gain in the genome. Analyses of rRNA sequences have confirmed that the SSU and LSU are the most common regions where self-splicing group I introns insert (Harris & Rogers, 2011; Yokoyama et al., 2002). Furthermore, the SSU rDNA has multiple non-random positions that are acceptable for group I intron insertion (Gargas et al., 1995; Simon et al., 2005; Xu et al., 2013). In lichenized fungi, multiple group I introns may exist in the SSU rDNA of an individual (Bhattacharya et al., 2000). Additionally, sometimes group I introns are useful for taxonomic studies at the genus or intra-genus level (Leavitt et al., 2011).
According to the data obtained in the present study, the group I intron at position 1769 was found in more than 90% of Endocarpon individuals, and these introns were divided into three clades, as shown in Figure 4. The ME trees of mycobiont and group I intron confirmed the similarity between the intron and mycobiont trees and suggested that group I intron could be used to identify species in Clade I, but not in Clade II and III. These findings confirm that group I introns can be applied to phylogenetic analysis, but their application has some limitations, which is consistent with previous studies (Mattsson et al., 2009). This work predicted the RNA secondary structure to reveal the conserved domain and its characteristics more clearly, as shown in Figure 5A-E. The main difference among introns was the P8 element; where the long type had a larger P8 region ranging in length from about 180-330 bps. However, the P8 element is not a conservative domain in group I introns and is more likely to undergo mutation or loss, without affecting the function of group I introns. It is particularly noteworthy that a 6 bp nucleotide sequence (AAGATA) at 3’ in the P8 element was extremely conserved, which may provide important information for further research on the polymorphism and evolution of the 1769 intron.
Moreover, the P3/P4 elements, along with other helix regions, also exhibited differences in different group I introns, as shown in Table 2. While medium-long groups exhibited similarity, the short groups showed significant differences. In a previous study of group I introns from 39 species in 27 genera belonging to the family Parmeliaceae, the position 1769 intron showed length variability at the family or genus level, with long, medium, and short groups being employed to distinguish them (Gutierrez et al., 2007). This study found length polymorphisms not only at the genus level but also at the species level, as shown in E. pusillum.
The study identified a particular group I intron from sample HL12Y014F that exhibited similarities in sequence conservation and clustering to other medium individuals, but shared similarities in intron length and secondary structure with the long group, which had a large P8 element (Fig. 5C). Since the secondary structure of the group I intron was more conservative than the primary structure, the group I intron from sample HL12Y014F was classified as the long type. This case may represent a transitional state in the evolution of the group I intron at 1769 in Endocarpon, providing insight into the evolution of group I introns in lichenized fungi. Furthermore, the 1769 intron of E. pusillum from Helan Mountain showed polymorphism, including all states (the long, medium, short, long-medium transition, and “none” states), making it the first report that group I introns are non-conservative at the same insertion site from the same species in the same habitat. This finding implies that the group I intron at this site underwent relatively fast evolution or horizontal transfer, undergoing a process of rapid gain and loss. This case undoubtedly provides a good model for the evolution of group I intron in lichenized fungi.
In summary, this study has uncovered a distinct co-dispersal strategy in lichens that differs from the conventional dispersal modes of sexual and asexual reproduction. The research highlights the influence of this co-dispersal strategy on shaping lichen population structure. Future investigations will delve into the evolutionary history of lichens, exploring the origin and molecular mechanisms underlying this unique co-dispersal strategy, as well as its impact on lichenization.
CY analyzed the data, constructed the figures, and drafted the manuscript. QZ and SC gathered the specimens, performed the biological assays and took part in the data analysis. YS and LL helped to construct the figures. YC and HT participated in drafting the manuscript. CL and QZ initiated and designed the study, participated in the data analysis, and finalized the manuscript. All authors read and approved the final version of the manuscript.
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.
This work was supported by the National Natural Science Foundation of China (grant number 41906201, 31000010), and by the National Infrastructure of Natural Resources for Science and Technology Program of China.
The authors are deeply grateful to the reviewers for their insightful feedback and constructive suggestions, which have greatly contributed to enhancing the quality of this manuscript.
The sequences generated for this study were deposited in GenBank (https://www.ncbi.nlm.nih.gov/genbank/; accession numbers are listed in Table 1).