Abstract
The delimitation of the invasive moss species Campylopus introflexus from its closest relative, Campylopus pilifer, has been long debated based on morphology. Previous molecular phylogenetic reconstructions based on the nuclear ribosomal internal transcribed spacers (ITS) 1 and 2 showed that C. pilifer is split into an Old World and a New World lineage, but remained partly inconclusive concerning the relationships between these two clades and C. introflexus. Analyses of an extended ITS dataset displayed statistically supported incongruence between ITS1 and ITS2. ITS1 separates the New World clade of C. pilifer from a clade comprising C. introflexus and the Old World C. pilifer. Ancestral state reconstruction showed that this topology is morphologically supported by differences in the height of the dorsal costal lamellae in leaf cross‐section (despite some overlap). ITS2, in contrast, supports the current morphological species concept, i.e., separating C. introflexus from C. pilifer, which is morphologically supported by the orientation of the hyaline hair point at leaf apex as well as costal lamellae height. Re‐analysis of published and newly generated plastid atpB‐rbcL spacer sequences supported the three ITS lineages. Ecological niche modeling proved a useful approach and showed that all three molecular lineages occupy distinct environmental spaces that are similar, but undoubtedly not equivalent. In line with the ITS1 topology, the C. pilifer lineage from the New World occupies the most distinct environmental niche, whereas the niches of Old World C. pilifer and C. introflexus are very similar. Taking the inferences from ecological niche comparisons, phylogenetics, and morphology together, we conclude that all three molecular lineages represent different taxa that should be recognized as independent species, viz. C. introflexus, C. pilifer (Old World clade), and the reinstated C. lamellatus Mont. (New World clade).
Keywords: Campylopus lamellatus, Campylopus pilifer, incongruence, integrative taxonomy, internal transcribed spacer, morphology
1. INTRODUCTION
Accurate species identification is of great importance, for example, in biodiversity assessments, conservation, but also to monitor species with invasive potential. In bryophytes, a morphological species concept is still most commonly employed (Shaw, 2009), but species identification is frequently hampered by relatively few and often (highly) variable morphological characters. This is especially true for species of large and taxonomically complex genera such as Campylopus Brid. Although extensive morphological revisions have reduced the number of Campylopus species from ca. 1,000 to about 150 (Frahm, 1999; and references therein; Frey & Stech, 2009), the circumscription and identification of many of these species remains difficult. This is especially pressing in delimiting the invasive species Campylopus introflexus (Hedw.) Brid. from its closest relatives.
Campylopus introflexus is one of the most aggressive invasive moss species (Essl, Steinbauer, Dullinger, Mang, & Moser, 2014) and probably the best known case of moss invasiveness in the world (Carter, 2014; Hassel & Söderström, 2005; Klinck, 2010). Originating from temperate areas of the southern Hemisphere, C. introflexus was first recorded outside its native range from Great Britain in 1941 (Richards, 1963) and spread quickly across Europe (Klinck, 2010; Størmer, 1958). Besides Europe, C. introflexus was introduced in North America (Carter, 2014). Its negative impact on the biodiversity of natural habitats such as coastal and inland dunes, especially lichen‐rich gray dunes (Essl et al., 2014; Klinck, 2010; Sparrius & Kooijman, 2011), should have brought attention to its troublesome delimitation from closely related species, especially Campylopus pilifer Brid. (Frahm, 1974; Frahm & Stech, 2006; Gradstein & Sipman, 1978). Morphologically, C. introflexus and C. pilifer can be distinguished by the different anatomy of the costa in leaf cross section as well as the orientation of the hyaline hairpoint at leaf apex (Frahm, 1991; Frahm & Stech, 2006; Gama, Faria, Câmara, & Stech, 2016). In C. pilifer, the dorsal costal lamellae are two to seven cell rows high and the hairpoint is straight, whereas C. introflexus is recognized by lamellae not higher than two cell rows and, when present, reflexed hair points. The effectiveness of using these and other morphological characters to delimit both species have been subject of debate for decades (e.g., Frahm, 1974, 1991; Frahm & Stech, 2006; Gradstein & Sipman, 1978; Stech & Dohrmann, 2004).
Assessing morphological species delimitations in Campylopus using molecular data is challenging. Chloroplast markers (atpB‐rbcL, trnT‐F, atpI‐atpH) provided little phylogenetic signal to delimit species (Stech, 2004), as also reported for other moss genera such as Dicranum Hedw. (Lang, Bocksberger, & Stech, 2015), and were partly difficult to sequence, especially at pB‐rbcL, the slightly more variable of the cpDNA markers. In contrast, the nuclear ribosomal internal transcribed spacer (ITS1‐5.8S‐ITS2) region, the most widely used nuclear marker for plant phylogenetic inferences (Stech & Quandt, 2010), is highly variable in Campylopus. Two main types of ITS1 were found, one in C. introflexus, C. pilifer from the Old World and the sister genus Pilopogon, and the other in the New World samples of C. pilifer and other Campylopus species (discussed in detail by Stech & Dohrmann, 2004). However, the weakly resolved maximum parsimony analyses of ITS1 and ITS2 separately in Stech and Dohrmann (2004) did not allow to fully assess the impact of different phylogenetic signals in both spacers on species relationships in Campylopus.
Incongruence between 18S and the internal transcribed spacers was reported by Durand et al. (2002) in the invasive green algal species Cauler paracemosa (Forsskål) J. Agardh, and paralogous ITS copies were found in the angiosperm family Calycanthaceae (Li, Ledger, Ward, & del Tredici, 2004); however, incongruence between ITS1 and ITS2, as observed in Campylopus has, to the best of our knowledge, not yet been found in any other group of land plants. In contrast to several other widespread Campylopus species, C. introflexus was shown to be monophyletic and well delimited based on ITS sequences, but its relationships with the two molecular lineages of C. pilifer remained ambiguous (Gama et al., 2016; Stech & Dohrmann, 2004; Stech, Sim‐Sim, & Kruijer, 2010; Stech & Wagner, 2005).
As Padial, Miralles, Dela Riva, and Vences (2010) have pointed out, consensus is emerging that species are separately evolving lineages of populations or metapopulations, and the decision that separate lineages should be recognized as distinct species should take into account a combination of different data and analysis methods (integrative taxonomy). Integrative taxonomic approaches combining molecular and morphological evidence have indeed shed new light on species delimitations in bryophytes (e.g., Caparrós, Lara, Draper, Mazimpaka, & Garilleti, 2016; Dirkse, Losada‐Lima, & Stech, 2016; Draper et al., 2015; Medina, Lara, Goffinet, Garilleti, & Mazimpaka, 2012; Sim‐Sim et al., 2017). In Campylopus, additional data sources are needed to assess both the molecular phylogenies and the morphological variability. In this study, we use ecological niche comparison techniques (Broennimann et al., 2012) to understand niche differences between the molecular lineages of C. pilifer and C. introflexus. We consider the niche as describing the set of biotic and abiotic conditions where a species can persist (Grinnell, 1917; Holt, 2009; Hutchinson, 1957), which is the niche concept important for understanding the large‐scale geographic distribution of species (Wiens et al., 2010). According to the competitive exclusion principle, no two species can occupy exactly the same niche space (cannot have equivalent niches) over a long period of time (Gause, 1934). Even in the case of niche conservatism, i.e., when species diversification is not driven by ecological speciation, closely related species tend to be ecologically similar, but not identical (e.g., Kozak & Wiens, 2006; López‐Alvarez et al., 2015). If the ecological niche evolves as part of the speciation process, patterns of ecological differentiation can be potentially useful for species delimitation (Martínez‐Gordillo, Rojas‐Soto, & Espinosa de losMonteros, 2010). In fact, there is growing evidence that ecological niche data can assist species delimitation in different groups of organisms, including vertebrates (e.g., Leaché et al., 2009; Martínez‐Gordillo et al., 2010; Raxworthy, Ingram, Rabibisoa, & Pearson, 2007), invertebrates (e.g., Gurgel‐Gonçalves, Ferreira, Rosa, Bar, & Galvao, 2011; Hawlitschek, Porch, Hendrich, & Balke, 2011), and, most recently, also land plants (e.g., Aguirre‐Gutiérrez, Serna‐Chavez, Villalobos‐Arámbula, Pérez de la Rosa, & Raes, 2015; Shrestha & Zhang, 2015). However, no such study has yet been performed in bryophytes.
Based on the ecological data, molecular analysis of extended datasets (phylogenetic analysis of nuclear ITS and haplotype analysis of plastid atpB‐rbcL sequences), and re‐evaluation of diagnostic morphological characters using ancestral state reconstruction, we aim to conclude about species delimitations of C. introflexus and C. pilifer.
2. MATERIALS AND METHODS
2.1. Taxon sampling
For molecular phylogenetic analysis, ITS sequences of 89 specimens of Campylopus and two of Pilopogon Brid. as outgroup representatives, were compiled. Of these, 67 were taken from own previous analyses (Gama et al., 2016; Stech, 2004; Stech & Dohrmann, 2004), three were downloaded from Genbank (one Campylopus pilifer and two C. pilifer subsp. vaporarius (De Not.) Brullo, Privitera & Puglisi, Spagnuolo, Terracciano, Puglisi, & Privitera, 2014), and 21 C. pilifer specimens (10 New World clade and 11 Old World clade) were newly sequenced. Fifteen specimens originally identified as other species (C. arctocarpus (Hornsch.) Mitt., C. aureonitens (Müll. Hal.) A. Jaeger, C. catarractilis (Müll. Hal.) Paris, C. concolor (Hook.) Brid., C. incrassatus Müll. Hal., C. julaceus A. Jaeger, C. pilifer, C. richardii Brid.) were renamed based on the molecular results, except C. catarractilis (see Section 4). AtpB‐rbcL spacer sequences were compiled for 38 Campylopus specimens (20 from Stech, 2004; Stech & Dohrmann, 2004; Frahm & Stech, 2006 and Gama et al., 2016; and 18 newly sequenced). Voucher information and Genbank accession numbers of the newly sequenced specimens are provided in Table 1. For ecological niche comparisons, voucher information from 1,242 additional collections of C. pilifer from the New and Old World as well as C. introflexus were obtained from different herbaria (L, MO, NY, SP and UB) and from the Global Biodiversity Information Facility (GBIF). Specimens were selected in order to cover the total distribution ranges of the three lineages as far as possible. Data from GBIF collected prior to 1990 were excluded to minimize errors, especially identification problems of older collections, considering that the taxonomic relationships between C. pilifer and C. introflexus started to be investigated in more detail from that decade onwards (Frahm, 1991, 1999; Frahm & Stech, 2006; Stech & Dohrmann, 2004).
Table 1.
Voucher information and GenBank accession numbers for the newly generated sequences of Campylopus species
| Specimen | Original identification | Voucher | Herbarium | Country | Accession number | ||
|---|---|---|---|---|---|---|---|
| ITS1 | ITS2 | atpB‐rbcL | |||||
| C. catarractilis C089 | — | RSA 106‐09 | L | South Africa | — | — | MF462375 |
| C. introflexus C113 | — | Van Zanten 99.06.53 | L | The Netherlands | — | — | MF462377 |
| C. introflexus NL257 | Gama s.n. | L | The Netherlands | — | — | MF462387 | |
| C. introflexus RS03 | — | Poloni et al. s.n. | L | Brazil | — | — | KU163137 |
| C. lamellatus C225 | C. pilifer | Stech 04‐056 | L | Portugal—Madeira | MF416336 | MF416357 | MF462383 |
| C. lamellatus C013 | C. pilifer | Greven & Khoeblal 4000/3 | L | Réunion | MF416329 | MF416350 | MF462372 |
| C. lamellatus 1016 | C. pilifer | Faria 1016 | UB | Brazil | MF416345 | MF416366 | — |
| C. lamellatus MG28 | C. pilifer | Câmara 2146 | UB | Brazil | MF416346 | MF416367 | — |
| C. lamellatus SP181 | C. pilifer | Soares 1838 | UB | Brazil | MF416349 | MF416370 | — |
| C. lamellatus MG68 | C. pilifer | Gama 176 | UB | Brazil | MF416347 | MF416368 | — |
| C. lamellatus C156 | C. pilifer | Greven & Khoeblal 4000/4 | L | Réunion | MF416332 | MF416353 | MF462381 |
| C. lamellatus Col119 | C. pilifer | Linares & Churchill 3608 | MO | Colombia | MF416344 | MF416365 | — |
| C. lamellatus SP69 | C. pilifer | Yano & Kirizawa 32896 | SP | Brazil | MF416348 | MF416369 | MF462388 |
| C. lamellatus C094 | C. pilifer | Weigend et al. 5832 | L | Peru | MF416330 | MF416351 | MF462376 |
| C. lamellatus C040 | C. pilifer | Frahm s.n. | L | Brazil | — | — | MF462373 |
| C. lamellatus C138 | C. pilifer | Allen 6298 | L | USA | — | — | MF462379 |
| C. pilifer C221 | — | Stech 04‐526a | L | Portugal—Madeira | MF416334 | MF416355 | — |
| C. pilifer C127 | — | Müller B816 | L | Equatorial Guinea | MF416331 | MF416352 | — |
| C. pilifer C231 | — | Frahm M‐9 | L | Portugal—Madeira | MF416337 | MF416358 | — |
| C. pilifer C236 | — | Luis s.n. | L | Portugal—Madeira | MF416340 | MF416361 | — |
| C. pilifer C242 | — | Stech ‐7‐023 | L | Portugal–Madeira | MF416342 | MF416363 | — |
| C. pilifer C224 | — | Stech 04‐037 | L | Portugal—Madeira | MF416335 | MF416356 | — |
| C. pilifer C235 | — | Luis s.n. | L | Portugal—Madeira | MF416339 | MF416360 | — |
| C. pilifer C241 | — | Stech 07‐008 | L | Portugal—Madeira | MF416341 | MF416362 | — |
| C. pilifer C211 | — | Frahm s.n. | L | France | MF416333 | MF416354 | — |
| C. pilifer C232 | — | Frahm M‐84 | L | Portugal—Madeira | MF416338 | MF416359 | — |
| C. pilifer C243 | — | Stech 07‐037 | L | Portugal—Madeira | MF416343 | MF416364 | — |
| C. pilifer C055 | — | Frahm 7611 | L | Rwanda | — | — | MF462374 |
| C. pilifer C124 | — | Van Zanten 01.08.01A | L | The Netherlands | — | — | MF462378 |
| C. pilifer C143 | — | Lindlar 458 | L | Cape Verde | — | — | MF462380 |
| C. pilifer C248 | — | Stech 07‐73b | L | Portugal—Madeira | — | — | MF462384 |
| C. pilifer C255 | — | Stech 07‐187 | L | Portugal—Madeira | — | — | MF462385 |
| C. pilifer C263 | — | Stech 08‐452 | L | Portugal—Madeira | — | — | MF462386 |
2.2. Phylogenetic analysis
Genomic DNA was extracted with the NucleoSpin Plant II Kit (Macherey‐Nagel, Düren, Germany). PCR amplification protocols followed Gama, Stech, Schäfer‐Verwimp, and Peralta (2015). Sequencing was performed by Macrogen, Inc. (www.macrogen.com). Sequences were aligned in Geneious R8 (Kearse et al., 2012). Gaps were treated as informative by simple indel coding (SIC) (Simmons & Ochoterena, 2000) using SeqState (Müller, 2004). No character or position was excluded from the analyses.
Separate phylogenetic analyses of ITS1 and ITS2 were performed under maximum likelihood (ML) and Bayesian inference (BI). The GTR+Γ model, selected under the Akaike information criterion in jModelTest2 (Darriba, Taboada, Doallo, & Posada, 2012; Guindon & Gascuel, 2003), was applied. Maximum likelihood trees were calculated withRaxML version 8.0.26 (Stamatakis, 2014) using raxmlGUI version 1.3.1 (Silvestro & Michalak, 2012). Bootstrap support (BS) values were obtained with a thorough bootstrap algorithm and 10,000 pseudoreplicates. Bayesian analyses were run using MrBayes version 3.2.5 (Ronquist et al., 2012). Bayesian posterior probabilities (PP) were estimated by the Markov Chain Monte Carlo (MCMC) method. Four runs with four chains each (three heated and one cold) were run with 30 × 106 generations, with chains sampled every 1,000th generation and the respective trees written to a tree file. A threshold of <0.01 for the standard deviation of split frequencies was used to assess convergence of runs. Fifty percent majority rule consensus trees and posterior probabilities of clades were calculated combining the four runs using the trees sampled after convergence of the chains and the “burn‐in” (25% of the trees) discarded.
Relationships among atpB‐rbcL haplotypes were evaluated based on statistical parsimony, using TCS version 1.21 (Clement, Posada, & Crandall, 2000), with gaps coded as missing data.
2.3. Ecological niche comparisons
We selected environmental data regarding eco‐physiological constraints of the target taxa according to recent literature on habitat preferences (Frahm & Stech, 2006; Klinck, 2010; Spagnuolo et al., 2014; Sparrius & Kooijman, 2011; Sparrius, Sevink, & Kooijman, 2012). The selected 10 environmental variables were obtained from WorldClim (www.worldclim.org) and are of high spatial and temporal resolution. The variables are derived from interpolation of weather stations data as described by Hijmans, Cameron, Parra, Jones, and Jarvis (2005) and are listed in Table 2. We included several components of temperature variation and precipitation variables to account for the different biomes within the area of occurrence and its constraints on the survival of the target taxa. All selected variables presented Pearson's correlation ≤0.70 (Dormann et al., 2013) and had a spatial resolution of 10 × 10 km at the equator.
Table 2.
Environmental variables used for ecological nichemodeling. WorldClim (Hijmans et al., 2005)
| Environmental variable |
|---|
| 1. Isothermality |
| 2. Temperature Seasonality |
| 3. Maximum temperature of the warmest month |
| 4. Minimum temperature of the coldest month |
| 5. Mean temperature of wettest quarter |
| 6. Mean temperature of driest quarter |
| 7. Precipitation of wettest month |
| 8. Precipitation of driest month |
| 9. Precipitation of driest quarter |
| 10. Precipitation of warmest quarter |
We calculated ecological niche characteristics in order to assess how much of the environmental niche space is shared between the molecular lineages of C. introflexus, C. pilifer from the New World and C. pilifer from the Old World. We used an ordination technique with kernel smoothers (Broennimann et al., 2012) to extract the ecological niche space that is occupied by each of the molecular lineages and to quantify niche overlap, equivalence and similarity. The number of occurrences used per molecular lineage may be biased and not representative for the total distribution of the taxa in the environmental space, possibly resulting in an incorrect estimation of their density. Therefore, a kernel density function was applied for smoothing the density of occurrences throughout each cell in the environmental space, leading to a better indication of the suitability of the environmental conditions per lineage. We performed the analyses using a principal component analysis calibrated on the whole environmental space of the study area (PCA‐ent). All analyses were carried out in R (R Development Core Team, 2014).
We obtained the niche breadth of each lineage (amount of ecological niche space available to the different lineages) by using the Levins’ inverse concentration metric (Levins, 1968). To quantify the niches shared by the Campylopus lineages, we computed the niche overlap under Schoener's D statistic from the ecological niche space (Schoener, 1968; Warren, Glor, & Turelli, 2008), under which the value of D ranges from 0 to 1 (0 meaning each two lineages have no overlap in the environmental space and 1 meaning they share the same environmental space).
The niche equivalence test was performed in order to assess whether the ecological niches of each pair of molecular lineages differed significantly from each other or were interchangeable. We compared the niche overlap values (D) of the pairs of molecular lineages to a null distribution of 100 overlap values. In case the niche overlap value of the molecular lineages being compared was significantly lower than those acquired by the null distribution (p < .05), we assumed the ecological niches not to be equivalent.
Considering that the test for niche equivalency test only assesses whether two species are identical in their niche space by using their exact locations, but disregards the surrounding space, we also performed a niche similarity test. This test assesses whether the ecological niches of any pair of species (in this case, lineages) are more different than would be expected by chance, and considers the differences in the surrounding environmental conditions in the geographic areas where both species are distributed (Warren, Glor, & Turelli, 2010).
We investigated the main environmental variables that constrain the distributions of the lineages based on the loadings of the first two axes of the PCA‐ent.
2.4. Ancestral state reconstructions
Two morphological characters that are considered most important to distinguish C. introflexus and C. pilifer, viz. the hyaline hairpoint at leaf apex and the height of the ventral costal lamellae in leaf cross section, were scored from the molecularly analyzed specimens. Mature leaves were removed from the stems and cross sections made with a razor blade. The highest costal lamella found in cross sections of the upper third of the lamina was scored for each specimen. We distinguished three character states of the hyaline hairpoint (absent, erect, reflexed), whereas for lamella height the measured values, ranging from 1 to 7 cells, were used as character states. Maximum likelihood ancestral state reconstructions of both characters were performed in Mesquite version 3.2 (Maddison & Maddison, 2016) under the one‐parameter Markov k‐state model (Lewis, 2001). Ancestral state reconstructions were based on the topologies of the Bayesian trees and carried out for ITS1 and ITS2 separately. We coded data as missing for the three samples for which ITS sequences were taken from GenBank.
3. RESULTS
3.1. Phylogenetic analysis
The ITS1 dataset comprised a total of 1,376 characters (alignment positions 1−1071, indels 1072−1376). The large number of alignment positions was mainly caused by the two main ITS1 types, which for large parts were separated in different blocks in the alignment. The Bayesian inference (BI) consensus tree from ITS1 is shown in Fig. 1, with posterior probabilities (PP) and maximum likelihood bootstrap support values (BS) at the branches. Two major clades were resolved. The first clade had maximum support (PP 1, BS 100%) and comprised the C. pilifer samples from the New World (the Americas) plus five samples from Réunion Island and one from Madeira Island. The second clade aggregated C. pilifer from the Old World, C. catarractilis, and C. introflexus with maximum support in the Bayesian analysis (PP 1). Campylopus introflexus was resolved as paraphyletic, with a clade of C. introflexus samples from mainly South America (Brazil and Paraguay) as sister to the clade of C. catarractilis, and the latter sister to C. pilifer from the Old World. The Old World C. pilifer clade was monophyletic with maximum support.
Figure 1.

Phylogram obtained from Bayesian analysis of nuclear ribosomal ITS1 sequences, including indels coded by simple indel coding. Values above branches are Bayesian posterior probabilities ≥0.95, values below branches are bootstrap support values ≥75% from maximum likelihood analysis of the same dataset
The ITS2 dataset comprised 881 characters (alignment positions 1−655, indels 656−881). The BI consensus tree obtained from ITS2 (Fig. 2) resolved two major clades within Campylopus, which corresponded to C. introflexus (including C. catarractilis, PP 1, BS 99%) and C. pilifer s.l. (Old World and New World clades, PP 0.98), respectively. In contrast to ITS1, in the ITS2 analyses, C. pilifer from the New World was resolved as paraphyletic to the C. pilifer Old World lineage. The latter received a PP of 1 but only moderate BS of 77%, and included four of the five samples from Réunion Island that in ITS1 were part of the New World clade with maximum support.
Figure 2.

Phylogram obtained from Bayesian analysis of nuclear ribosomal ITS2 sequences, including indels coded by simple indel coding. Values above branches are Bayesian posterior probabilities ≥0.95, values below branches are bootstrap support values ≥75% from maximum likelihood analysis of the same dataset. Branches with the symbol “//” were shortened four times
All included Old World C. pilifer specimens as well as four specimens from Réunion shared the same atpB‐rbcL haplotype (Fig. 3). Sequence divergence was higher within C. introflexus and the C. pilifer from the New World (three haplotypes each). In addition, C. introflexus displayed the A‐type loop inversion in the middle part of the spacer, in contrast to the T‐type in C. pilifer (cf. details in Stech, 2004), and all three lineages displayed different numbers of AT repeats in a microsatellite region in the spacer.
Figure 3.

Haplotype network inferred from chloroplast atpB‐rbcL spacer sequences using TCS. Circle sizes are an approximate representation of the number of specimens belonging to each haplotype. Squares comprise haplotypes belonging to the same species. The black dot indicates a hypothetical haplotype
3.2. Ecological niche comparisons
The distributions of the three molecular Campylopus lineages (C. introflexus, C. pilifer Old World, C. pilifer New World) are related to different responses to the environment and resulted in distinct distributions in niche space (Fig. 4). The analysis of ecological niche properties showed that the two first axes of the PCA‐ent were able to explain 79.95% of the variance of the data. The first axis was determined mostly by temperature‐related bioclimatic factors (namely isothermality, minimum temperature of coldest month, mean temperature of driest quarter, mean temperature of wettest quarter and maximum temperature of warmest month), accounting for 54% of the total variation in environmental conditions for the taxa in the study area (Fig. 4). The highest axis loadings where observed for minimum temperature of coldest month (0.41), isothermality (0.39), and temperature seasonality (0.38). The second axis accounted for 25.95% of the variation and was mainly loaded by precipitation of driest month (0.53), precipitation of driest quarter (0.53) and precipitation of the warmest quarter (0.39). The assessment of niche overlap revealed a small overlap in the environmental space of the three Campylopus lineages (Table 3). The C. pilifer lineage from the New World occupied the most distinct environmental niche when compared to the other two lineages (Table 3). The pairwise niche similarity comparison between the C. pilifer New and Old World lineages indicated that their niche overlap falls within the 95% confidence limits of the null distributions (p > .05), leading to non‐rejection of the hypothesis of retained niche similarity (Table 3). The niche similarity between the C. pilifer New World clade and C. introflexus clade was higher than expected by chance. The niche similarity between the C. pilifer Old World lineage and C. introflexus was higher than expected by chance in one direction only, indicating that the niche of the Old World clade was more similar than expected by chance to the one of C. introflexus, but not vice versa. In contrast, the niche equivalency was rejected for all pairwise comparisons, which indicates that the lineages underwent significant alteration of their distribution in environmental niche space along the process of colonization of the areas within their current distribution.
Figure 4.

Ecological niches of three distinct molecular lineages of Campylopus in environmental space produced by the principal component analysis method (PCA‐ent). The PCA‐ent result represents the climatic niche of the species in the two main axes with the environmental conditions of the complete study area. For each lineage, the gray‐to‐black shading represents the grid cell density of the species’ occurrences (black being the highest density). Dashed and solid lines represent 50% and 100% of the available environment, respectively. (a) PCA with axis 1 explaining 54% of the variance and axis 2 explaining 25.95%. (b) C. lamellatus. (c) C. pilifer. (d) C. introflexus. ISO: Isothermality. MaxTWM, Maximum temperature of warmest month; MinTCM, Minimum temperature of coldest month; MTDQ, mean temperature of driest quarter; MTWQ, mean temperature of wettest quarter; PDM, precipitation of driest month; PDQ, precipitation of driest quarter; PWM, precipitation of wettest month; PWQ, precipitation of warmest quarter; TS, temperature seasonality
Table 3.
Ecological niche comparisons (niche overlap, similarity, and equivalency) for pairwise comparisons of three molecular lineages of Campylopus (C. introflexus, C. pilifer Old World, and C. pilifer New World). ‘ns’ not significantly different. The ecological niches can be significantly (p < .05) more similar or different than expected by chance. p Values are given between parenthesis
| Comparison | Niche overlap (D) | Niche similarity a → b | Niche similarity b → a | Niche equivalency |
|---|---|---|---|---|
| (a) C. pilifer New World | 0.321 | ns | ns | Different |
| (b) C. pilifer Old World | (0.08) | (0.06) | (0.02) | |
| (a) C. pilifer New World | 0.397 | Similar | Similar | Different |
| (b) C. introflexus | (0.02) | (0.04) | (0.02) | |
| (a) C. pilifer Old World | 0.475 | Similar | ns | Different |
| (b) C. introflexus | (0.02) | (0.06) | (0.02) |
3.3. Ancestral state reconstructions
Reflexed hyaline hairpoints were restricted to C. introflexus, whereas erect hairpoints occurred in both C. pilifer lineages and in C. catarractilis (Figs 5 and 6). Apart from the outgroup, the hairpoint was rarely scored as absent, only in three C. introflexus specimens as well as a single specimen of C. pilifer from the New World. The ITS1 topology suggests that both the reflexed and erect hairpoint states have arisen more than once in the evolutionary history (Fig. 5), whereas in the ITS2 topology the distribution of both character states is in accordance with the current understanding of the species delimitations. Here, with the exception of C. catarractilis, the reflexed hyaline hairpoint is resolved as a synapomorphy of C. introflexus and the erect hairpoint as a synapomorphy for the two C. pilifer lineages. Low costal lamellae (1–2 cell rows high) were restricted to C. introflexus and C. catarractilis (Figs 5 and 6). In general, the New World clade of C. pilifer displayed longer lamellae than the Old World clade. However, homoplasy between the two lineages of C. pilifer was observed under the ITS1 topology due to overlapping character states. The ITS2 topology supports a gradual decrease in lamellae height in C. pilifer, from long lamellae in the clades branching off first (corresponding to the New World clade) to shorter lamellae in most subclades of the Old World clade.
Figure 5.

Maximum likelihood ancestral state reconstruction of lamellae height and hairpoint on ITS1
Figure 6.

Maximum likelihood ancestral state reconstruction of lamellae height and hairpoint on ITS2
4. DISCUSSION
The model‐based analyses of the present ITS dataset resulted in well‐resolved and supported phylogenetic reconstructions, which allow to assess the different phylogenetic signals of ITS1 and ITS2 in the studied Campylopus species more precisely than the maximum parsimony analyses in Stech and Dohrmann (2004). In fact, both internal transcribed spacers display statistically supported incongruence. ITS1 separates the New World clade of C. pilifer from a clade comprising C. introflexus and the Old World C. pilifer (Fig. 1), whereas ITS2 separates C. introflexus from C. pilifer s.l. (Fig. 2). Further incongruence is observed concerning the positions of C. catarractilis as well as four samples from Réunion Island. The ITS2 thus seems to coincide with the current morphological species concept of C. introflexus and C. pilifer s.l., which is supported by the distribution of reflexed versus straight hairpoints at leaf apex as well as costal lamellae 1−2 versus >2 cell rows high in the ancestral state reconstructions (Fig. 6). The ITS1 topology, however, seems to be supported by morphology as well, separating specimens with costal lamellae (4−)5−6 cell rows high (New World C. pilifer) from specimens with mostly lower lamellae, namely 1(−2) cell rows in C. introflexus and 3−4(−6) cell rows in Old World C. pilifer (Fig. 5).
The presence of conflicting ITS‐based hypotheses and morphological support for each of the ITS lineages, but also the observed overlap in lamellae height at least in some specimens, indicate that it is important to consider other sources of biological information to delimit Campylopus introflexus and C. pilifer. Despite the smaller number of plastid atpB‐rbcL sequences analyzed here and the low resolution of earlier phylogenetic trees based on plastid sequences, the haplotype network approach supports the existence of the three lineages, C. introflexus, New World C. pilifer, and Old World C. pilifer (Fig. 3), without mixing of haplotypes except for the same four samples from Réunion Island that also deviate with ITS. Furthermore, ecological niche comparison proved a useful approach and showed that all three molecular lineages occupy distinct environmental spaces that are similar, but undoubtedly not equivalent (Table 3, Fig. 4). In line with the ITS1 topology, the C. pilifer lineage from the New World occupied the most distinct environmental niche, whereas the C. pilifer Old World lineage and C. introflexus occupied very similar niche spaces.
The inferences from ecological niche comparisons, phylogenetic analyses, and assessment of morphological characters together indicate that all three molecular lineages represent different taxa. We consider the present integrative data sufficient to formally distinguish the three lineages as independent species, viz. C. introflexus, C. pilifer (Old World clade), and the reinstated species C. lamellatus Mont. (New World clade; see Section 5). According to the present data, ITS1 has a discriminatory power to resolve C. lamellatus, whereas ITS2 resolves C. introflexus, and C. pilifer is monophyletic based on both internal transcribed spacers, and the atpB‐rbcL spacer may serve as a suitable DNA barcode marker for molecular identification of all three species. However, we acknowledge that the observed patterns and the resulting taxonomic treatment should be tested based on more markers from different genomes in the future. Morphologically, the three species can be distinguished by the combination of hairpoint orientation and height of the dorsal costal lamellae, with C. introflexus being most easily recognized, whereas C. lamellatus and C. pilifer are more overlapping. Ecologically, C. lamellatus is most distinct.
As far as the geographical separation of C. lamellatus and C. pilifer is concerned, already Stech and Dohrmann (2004) and Stech et al. (2010) observed that the former spreads out to oceanic islands of the Old World, namely Madeira Island and Réunion Island. Whereas the specimen from Madeira (C225) and one specimen from Réunion (C156) are part of the C. lamellatus clade based on both ITS1 and ITS2 in the present study, the remaining four samples from Réunion Island (C013, C120, C121, C122) share ITS2 sequences with the C. pilifer Old World clade. Morphologically, these four samples belong to C. lamellatus according to their costal lamellae 5–6 cell rows high. The discrepant phylogenetic results between both internal transcribed spacers suggest that hybridization has possibly occurred between C. lamellatus and C. pilifer. This is supported by the atpB‐rbcL spacer sequences of samples C013, C120, C121, and C122, which all belong to C. pilifer. Since the plastid DNA is maternally inherited, C. pilifer seems to be the maternal ancestor of the putative hybrid specimen on Réunion. However, further analyses based on a larger taxon and marker sampling is necessary.
Gradstein and Sipman (1978) considered the type specimen of Campylopus lamellatus an extreme expression of a general tendency of longer costal lamellae in plants from tropical mountain areas, which had very slender shoots with distinct comal heads, but otherwise fit C. pilifer. Consequently, they reduced C. lamellatus to a subspecies of C. pilifer. Frahm (1985a) assumed a correlation between lamella height and habitat as well, with C. introflexus (shorter lamellae) occurring on wetter places than C. pilifer (longer lamellae) in regions where both species occur together. Frahm (1985a) furthermore supposed the lamellae in C. lamellatus to be longer to enhance gas exchange in rainforests with high temperature and high air humidity. However, the present molecular data indicate that lamellae 5−6 cell rows high have a genetic basis and are not merely modifications due to environmental conditions, at least in C. lamellatus. In fact, the specimens of the C. lamellatus clade were collected from a broad elevation range (100 to >3,000 m), not only from tropical montane rainforests, but also from very different habitats such as open vegetation with grasses (specimen C120, Réunion), mesquite‐oak savanna (C057, Texas, USA), savanna field among giant Vellozia sp. populations (MG68, Minas Gerais, Brazil), Pinus‐Juniperus forest (C058, Georgia, USA), or the Madeiran laurel forest (C225). In C. pilifer, the present data do not indicate a correlation between habitat or geographic area and lamellae height, either. For example, the specimens from the Azores differ considerably in this character (lamellae 3−6 cell rows high). Whether the presence of higher lamellae in both C. lamellatus and C. pilifer is a result of convergent evolution, possibly as an adaptation to microclimatic conditions, needs further investigation.
Other intraspecific taxa distinguished within the former C. pilifer s.l. molecularly clearly belong to the C. pilifer Old World clade (Figs 1 and 2), viz. C. pilifer var. brevirameus (Dix.) J.‐P. Frahm & Stech, which is morphologically closest to C. introflexus in its short lamellae, but differs by the erect hair point (Frahm & Stech, 2006), and C. pilifer subsp. vaporarius, confined to volcanic fumaroles in Italy. The latter has dorsal lamellae 2−3 (rarely 4) cell rows high, and both erect and reflexed hyaline hair points, even on the same stem (Spagnuolo et al., 2014). No molecular data are available yet from C. pilifer subsp. galapagensis (J.‐P. Frahm & Sipman) J.‐P. Frahm, another narrow endemic described from volcanic rock in Galapagos, which has dorsal lamellae 2−3 cell rows high but differs by the presence of ventral substereids instead of hyalocysts in costa cross section, possible as adaptation to drier habitats (Frahm, 1991).
The present results support recent studies from other groups of organisms indicating that ecological niche comparisons can improve our understanding of the delimitation and relationships of (closely related) species. For example, Aguirre‐Gutiérrez et al. (2015) showed that closely related taxa of Pinus subgenus Strobus have similar, but not equivalent ecological niches, indicating that they are indeed different species. Shrestha and Zhang (2015) failed to separate taxa of the Huperziaserrata (Thunb.) Trevis. species complex based on morphological data alone. However, using an integrative approach of morphological analysis together with distribution modeling and niche information tests for similarity and equivalency, they were able to circumscribe the different species of the complex. When proposing species circumscriptions of horned lizard (genus Phrynosoma) based on molecular phylogenetics, Leaché et al. (2009) retrieved five distinct evolutionary lineages by mtDNA. Nonetheless, when combined with nrDNA, their analyses recovered three lineages, which were further confirmed by morphology and climatic niche models. Similarly, we found that revisiting morphology after the ecological and molecular analyses resulted in a more thorough approach to understand species circumscriptions. In accordance with Raxworthy et al. (2007) and Hawlitschek et al. (2011), we conclude that ecological niche assessments can aid significantly in delimiting species with difficult taxonomic histories, where it can help build a strong case for lumping or splitting species, in combination with other sources of data.
The improved understanding of the delimitations of C. introflexus, C. lamellatus, and C. pilifer is expected to facilitate the identification of collected specimens. This will be particularly helpful to assess the native distribution area of C. introflexus and monitor its distribution in areas where it is invasive. With the exception of the C. catarractilis specimen, all analyzed specimens originally identified as other Campylopus species could be assigned to one of the three species. Similar percentages of misidentified specimens in Campylopus (15%, present study) and the Racomitrium canescens species complex (20%; Stech et al., 2013) indicate that a percentage of 15%−20% may be expected when analyzing morphologically identified specimens of closely related bryophyte species in an integrative approach.
The African species Campylopus catarractilis has not been considered closely related to either C. introflexus or C. pilifer (cf. Frahm, 1985b). The incongruent position of C. catarractilis (sister to C. pilifer based on ITS1 and nested in C. introflexus based on ITS2) suggested that the sequenced specimen might be misidentified and of hybrid origin similar to the specimens from Réunion discussed above. However, the combination of morphological characters of an erect hairpoint, low lamellae, and the typical serrate leaf apex as diagnostic character for C. catarractilis (Frahm, 1985b) in the sequenced specimen, did not allow to unambiguously assign it to either C. introflexus or C. pilifer. Analysis of further C. catarractilis specimens is necessary to infer its taxonomic status.
Despite new insights, further morphological traits should be explored to find additional diagnostic characters that facilitate morphological identification of C. introflexus, C. lamellatus, and C. pilifer. Two observations concerning the costa cross‐section not yet mentioned in the literature were made during this study. Firstly, a group of stereid cells is found above each dorsal lamella intercalated with a larger sub‐stereid cell, except in the center of the leaves where two stereid groups are fused without a sub‐stereid cell between them. This causes the two central lamellae to fuse as well and grow in a V‐shaped orientation. This V‐shaped pattern is more conspicuous when the lamellae are higher and therefore easier to be seen in C. lamellatus and C. pilifer. Secondly, a marked difference in the delimitation of the costa was observed, which is gradual in C. pilifer, most C. lamellatus, and C. introflexus p.p., but abrupt in a well‐supported clade within C. introflexus, a few C. lamellatus and in C. catarractilis. Despite the fact that these characters do not clearly delimit the molecular lineages, these observations indicate that the morphological and anatomical characters within Campylopus are not yet fully employed and that there is potential of novel characters to be found.
Global moss diversity analyses are still hampered by taxonomic and spatial distribution knowledge gaps, particularly in the tropics (Geffert, Frahm, Barthlott, & Mutke, 2013). The impact of misunderstood species delimitations, and misidentifications based on morphology, on species distribution patterns was recently demonstrated for Brazil, where it was understood by the bryological community that no C. introflexus occurred in the country, and that all piliferous Campylopus specimens belonged to C. pilifer. Gama et al. (2016), however, revealed that both species have an overlapping distribution in many places of South America, including Brazil. These findings have immediate impact on the checklist of bryophytes of Brazil, which has not recognized C. introflexus yet (Costa et al., 2011). A similar situation may occur in Australia and New Zealand, where currently only C. introflexus is reported. Considering the potential distribution of C. pilifer and a possible identification bias, it seems likely that C. pilifer will be found to occur in Australasia as well, but further investigation is necessary. In accordance with Silva, Vilela, De Marco, and Nemésio (2014), we have shown that ecological niche assessments can aid in the understanding of “data deficient” species.
5. TAXONOMIC TREATMENT
Campylopus lamellatus Mont. in Ann. Sci. Nat., Bot., sér. 29: 52. 1838.
Type: Bolivia, Chupé, Yungas, d'Orbignys.n. (holotype: PC, isotype: K in BM).
Campylopus pilifer var. lamellatus (Mont.) Gradst. &Sipman in Bryologist 81: 119. 1978.
Dicranum lamellatum (Mont.) Müll. Hal. in Syn. Musc. Frond. 1: 411. 1848.
ACKNOWLEDGMENTS
We thank CAPES (Brazilian Education agency) for financing the PhD project of the first author as well as the current study. We thank the curators of herbaria MO, NY, SP and UB for loan of specimens.
CONFLICT OF INTEREST
None declared.
Gama R, Aguirre‐Gutiérrez J, Stech M. Ecological niche comparison and molecular phylogeny segregate the invasive moss species Campylopus introflexus (Leucobryaceae, Bryophyta) from its closest relatives. Ecol Evol. 2017;7:8017–8031. https://doi.org/10.1002/ece3.3301
REFERENCES
- Aguirre‐Gutiérrez, J. , Serna‐Chavez, H. M. , Villalobos‐Arámbula, A. R. , Pérez de la Rosa, J. A. , & Raes, N. (2015). Similar but not equivalent: Ecological niche comparison across closely related Mexican white pines. Diversity and Distributions, 21, 245–257. [Google Scholar]
- Broennimann, O. , Fitzpatrick, M. C. , Pearman, P. B. , Petitpierre, B. , Pellissier, L. , Yoccoz, N. G. , … Guisan, A. (2012). Measuring ecological niche overlap from occurrence and spatial environmental data. Global Ecology and Biogeography, 21, 481–497. [Google Scholar]
- Caparrós, R. , Lara, F. , Draper, I. , Mazimpaka, V. , & Garilleti, R. (2016). Integrative taxonomy sheds light on an old problem: The Ulotacrispa complex (Orthotrichaceae, Musci). Botanical Journal of the Linnean Society, 180, 427–451. [Google Scholar]
- Carter, B. E. (2014). Ecology and distribution of the introduced moss Campylopus introflexus (Dicranaceae) in western North America. Madroño, 61, 82–86. [Google Scholar]
- Clement, M. , Posada, D. , & Crandall, K. A. (2000). TCS: A computer program to estimate gene genealogies. Molecular Ecology, 9, 1657–1659. [DOI] [PubMed] [Google Scholar]
- Costa, D. P. , Pôrto, K. C. , Luizi‐Ponzo, A. P. , Ilkiu‐Borges, A. L. , Bastos, C. J. P. , Câmara, P. E. A. S. , … Churchill, S. P. (2011). Synopsis of the Brazilian moss flora: Checklist, distribution and conservation. Nova Hedwigia, 93, 277–334. [Google Scholar]
- Darriba, D. , Taboada, G. L. , Doallo, R. , & Posada, D. (2012). jModelTest 2: More models, new heuristics and parallel computing. Nature Methods, 9, 772. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Dirkse, G. M. , Losada‐Lima, A. , & Stech, M. (2016). Riccia boumanii Dirkse, Losada & M.Stechsp. nov. (Ricciaceae, Marchantiophyta) in the Canary Islands, the first species of Riccia subgenus Ricca section Pilifer Volk outside South Africa. Journal of Bryology, 38, 94–102. [Google Scholar]
- Dormann, C. F. , Elith, J. , Bacher, S. , Buchmann, C. , Carl, G. , Carré, G. , … Lautenbach, S. (2013). Collinearity: A review of methods to deal with it and a simulation study evaluating their performance. Ecography, 36, 27–46. [Google Scholar]
- Draper, I. , Hedenäs, L. , Stech, M. , Patiño, J. , Werner, O. , González‐Mancebo, J. M. , … Ros, R. M. (2015). How many species of Isothecium (Lembophyllaceae, Bryophyta) are there in Macaronesia? A survey using integrative taxonomy. Botanical Journal of the Linnean Society, 177, 418–438. [Google Scholar]
- Durand, C. , Manuel, M. , Boudouresque, C. F. , Meinesz, A. , Verlaque, M. , & Le Parco, Y. (2002). Molecular data suggest a hybrid origin for the invasive Caulerparacemosa (Caulerpales, Chlorophyta) in the Mediterranean Sea. Journal of Evolutionary Biology, 15, 122–133. [Google Scholar]
- Essl, F. , Steinbauer, K. , Dullinger, S. , Mang, T. , & Moser, D. (2014). Little, but increasing evidence of impacts by alien bryophytes. Biological Invasions, 16, 1175–1184. [Google Scholar]
- Frahm, J.‐P. (1974). ZurUnterscheidung und Verbreitung von Campylopus introflexus (Hedw.) Brid. und C. polytrichoides De Not. Revue bryologique et lichénologiqueT. XL, Fasc., 1, 33–44. [Google Scholar]
- Frahm, J.‐P. (1985a). The ecological significance of the costal anatomy in the genus Campylopus . Abstracta Botanica, 9 (Suppl. 2), 159–169. [Google Scholar]
- Frahm, J.‐P. (1985b). Afrikanische Campylopus‐Arten. Bryophytorum Bibliotheca, 31, 1–216. [Google Scholar]
- Frahm, J.‐P. (1991). Campylopodioideae, Paraleucobryoideae. Flora Neotropica, Monograph, 54, 1–238. [Google Scholar]
- Frahm, J.‐P. (1999). A type catalogue of Campylopodioideae and Paraleucobryoideae (Musci, Dicranaceae), Part II, Campylopus . Tropical Bryology, 16, 17–102. [Google Scholar]
- Frahm, J.‐P. , & Stech, M. (2006). The taxonomic status of intermediate forms of Campylopus introflexus (Hedw.) Brid. and C. pilifer Brid. (Dicranaceae, Bryopsida) newly discovered in Europe. Cryptogamie Bryologie, 27, 213–223. [Google Scholar]
- Frey, W. , & Stech, M. (2009). Marchantiophyta, Bryophyta, Anthocerotophyta In Frey W. (Ed.), Syllabus of plant families. A. Engler′s Syllabus der Pflanzenfamilien, 13th ed., Part 3 Bryophytes and seedless vascular plants (pp. 13–263). Stuttgart: Gebr. BorntraegerVerlagsbuchhandlung. [Google Scholar]
- Gama, R. , Faria, A. L. A. , Câmara, P. E. A. S. , & Stech, M. (2016). Identity and origin of Campylopus (Leucobryaceae, Bryopsida) species from Trindade Island (Brazil). Cryptogamie Bryologie, 37, 241–250. [Google Scholar]
- Gama, R. , Stech, M. , Schäfer‐Verwimp, A. , & Peralta, D. F. (2015). A morpho‐molecular revision of Leucoloma (Dicranaceae, Bryophyta) in Brazil. Nova Hedwigia, 100, 319–332. [Google Scholar]
- Gause, I. (1934). The Struggle for Existence. Baltimore, MD: Williams & Wilkins. [Google Scholar]
- GBIF (2013). Global biodiversity information facility. Retrieved from www.gbif.org Accessed 12 June 2015.
- Geffert, J. L. , Frahm, J.‐P. , Barthlott, W. , & Mutke, J. (2013). Global moss diversity: Spatial and taxonomic patterns of species richness. Journal of Bryology, 35, 1–11. [Google Scholar]
- Gradstein, S. R. , & Sipman, H. J. M. (1978). Taxonomy and world distribution of Campylopus introflexus and C. pilifer (= C. polytrichoides): A new synthesis. Bryologist, 81, 114–121. [Google Scholar]
- Grinnell, J. (1917). The niche relationships of the California thrasher. The Auk, 34, 427–433. [Google Scholar]
- Guindon, S. , & Gascuel, O. (2003). A simple, fast and accurate method to estimate large phylogenies by maximum‐likelihood. Systematic Biology, 52, 696–704. [DOI] [PubMed] [Google Scholar]
- Gurgel‐Gonçalves, R. , Ferreira, J. B. C. , Rosa, A. F. , Bar, M. E. , & Galvao, C. (2011). Geometric morphometrics and ecological niche modelling for delimitation of near‐sibling triatomine species. Medical and Veterinary Entomology, 25, 84–93. [DOI] [PubMed] [Google Scholar]
- Hassel, K. , & Söderström, L. (2005). The expansion of the alien mosses Orthodontiumlineare and Campylopus introflexus in Britain and continental Europe. Journal of the Hattori Botanical Laboratory, 97, 183–193. [Google Scholar]
- Hawlitschek, O. , Porch, N. , Hendrich, L. , & Balke, M. (2011). Ecological niche modelling and nDNAsequencing support a new, morphologically cryptic beetle species unveiled by DNA barcoding. PLoS ONE, 6(2), e16662 https://doi.org/10.1371/journal.pone.0016662 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Hijmans, R. J. , Cameron, S. E. , Parra, J. L. , Jones, P. G. , & Jarvis, A. (2005). Very high resolution interpolated climate surfaces for global land areas. International Journal of Climatology, 25, 1965–1978. [Google Scholar]
- Holt, R. D. (2009). Bringing the Hutchinsonian niche into the 21st century: Ecological and evolutionary perspectives. Proceedings of the National Academy of Sciences of the United States of America, 106, 19659–19665. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Hutchinson, G. E. (1957). Concluding remarks. Cold spring harbor symposia on quantitative biology 22:415–427; Reprinted in 1991: Classics in theoretical biology. Bulletin of Mathematical Biology, 53, 193–213. [Google Scholar]
- Kearse, M. , Moir, R. , Wilson, A. , Stones‐Havas, S. , Cheung, M. , Sturrock, S. , … Drummond, A. (2012). Geneious Basic: An integrated and extendable desktop software platform for the organization and analysis of sequence data. Bioinformatics, 28, 1647–1649. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Klinck, J. (2010). NOBANIS – Invasive alien species fact sheet – Campylopus introflexus. Online Database of the European Network on Invasive Aliens Species. Retrieved from www.nobanis.org. Accessed 1 September 2015.
- Kozak, K. H. , & Wiens, J. J. (2006). Does niche conservatism promote speciation? A case study in North American salamanders. Evolution, 60, 2604–2621. [PubMed] [Google Scholar]
- Lang, A. , Bocksberger, G. , & Stech, M. (2015). Phylogeny and species delimitations in European Dicranum (Dicranaceae, Bryophyta). Molecular Phylogenetics and Evolution, 92, 217–225. [DOI] [PubMed] [Google Scholar]
- Leaché, A. D. , Koo, M. S. , Spencer, C. L. , Papenfuss, T. J. , Fisher, R. N. , & McGuire, J. A. (2009). Quantifying ecological, morphological, and genetic variation to delimit species in the coast horned lizard species complex (Phrynosoma). Proceedings of the National Academy of Sciences of the United States of America, 106, 12418–12423. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Levins, R. (1968). Evolution in changing environments: Some theoretical explorations. Princeton, NJ: Princeton University Press. [Google Scholar]
- Lewis, P. O. (2001). A likelihood approach to estimating phylogeny from discrete morphological character data. Systematic Biology, 50, 913–925. [DOI] [PubMed] [Google Scholar]
- Li, J. , Ledger, J. , Ward, T. , & del Tredici, P. (2004). Phylogenetics of Calycanthaceae based on molecular and morphological data, with a special reference to divergent paralogues of the nrDNA ITS region. Harvard Papers in Botany, 9, 69–82. [Google Scholar]
- López‐Alvarez, D. , Manzaneda, A. J. , Rey, P. J. , Giraldo, P. , Benavente, E. , Allainguillaume, J. , … Catalán, P. (2015). Environmental niche variation and evolutionary diversification of the Brachypodium distachyon grass complex species in their native circum‐Mediterranean range. American Journal of Botany, 102, 1073–1088. [DOI] [PubMed] [Google Scholar]
- Maddison, W. P. , & Maddison, D. R. (2016). Mesquite: a modular system for evolutionary analysis. Version 3.2. Retrieved from http://mesquiteproject.org.
- Martínez‐Gordillo, D. , Rojas‐Soto, O. , & Espinosa de losMonteros, A. (2010). Ecological niche modelling as an exploratory tool for identifying species limits: An example based on Mexican muroid rodents. Journal of Evolutionary Biology, 23, 259–270. [DOI] [PubMed] [Google Scholar]
- Medina, R. , Lara, F. , Goffinet, B. , Garilleti, R. , & Mazimpaka, V. (2012). Integrative taxonomy successfully resolved the pseudo‐cryptic complex of the disjunct epiphytic moss Orthotrichum consimile s.l. (Orthotrichaceae). Taxon, 61, 1180–1198. [Google Scholar]
- Müller, K. (2004). SeqState – Primer design and sequence statistics for phylogenetic DNA data sets. Applied Bioinformatics, 4, 65–69. [DOI] [PubMed] [Google Scholar]
- Padial, J. M. , Miralles, A. , Dela Riva, I. , & Vences, M. (2010). The integrative future of taxonomy. Frontiers in Zoology, 2010(7), 16. [DOI] [PMC free article] [PubMed] [Google Scholar]
- R Development Core Team (2014). R: A language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing; Retrieved from http://www.R-project.org. [Google Scholar]
- Raxworthy, C. J. , Ingram, C. M. , Rabibisoa, N. , & Pearson, R. G. (2007). Applications of ecological niche modeling for species delimitation: A review and empirical evaluation using day geckos (Phelsuma) from Madagascar. Systematic Biology, 56, 907–923. [DOI] [PubMed] [Google Scholar]
- Richards, P. W. (1963). Campylopus introflexus (Hedw.) Brid. and C. polytrichoides De Not. in the British Isles; a preliminary account. Transactions of the British Bryological Society, 4, 404–417. [Google Scholar]
- Ronquist, F. , Teslenko, M. , Mark, P. V. D. , Ayres, D. L. , Darling, A. , Höhna, S. , … Huelsenbeck, J. P. (2012). MrBayes 3.2: Efficient Bayesian phylogenetic inference and model choice across a large model space. Systematic Biology, 61, 539–542. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Schoener, T. W. (1968). The Anolis lizards of Bimini: Resource partitioning in a complex fauna. Ecology, 49, 704–726. [Google Scholar]
- Shaw, A. J. (2009). Bryophyte species and speciation In Goffinet B., & Shaw A. J. (Eds.), Bryophyte Biology, 2nd ed Cambridge: Cambridge University Press. [Google Scholar]
- Shrestha, N. , & Zhang, X.‐C. (2015). Recircumscription of Huperziaserrata complex in China using morphological and climatic data. Journal of Systematics and Evolution, 53, 88–103. [Google Scholar]
- Silva, D. P. , Vilela, B. , De Marco, P. Jr. , & Nemésio, A. (2014). Using ecological niche models and niche analyses to understand speciation patterns: The case of sister Neotropical orchid bees. PLoS ONE, 9(11), e113246 https://doi.org/10.1371/journal.pone.0113246 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Silvestro, D. , & Michalak, I. (2012). raxmlGUI: A graphical front‐end for RaxML. Organisms, Diversity, and Evolution, 12, 335–337. [Google Scholar]
- Simmons, M. P. , & Ochoterena, H. (2000). Gaps as characters in sequence‐based phylogenetic analyses. Systematic Biology, 49, 369–381. [PubMed] [Google Scholar]
- Sim‐Sim, M. , Afonina, O. M. , Almeida, T. , Désamoré, A. , Laenen, B. , Garcia, C. A. , … Stech, M. (2017). Integrative taxonomy reveals too extensive lumping and a new species in the moss genus Amphidium (Bryophyta). Systematics and Biodiversity, 15, 451–463. DOI: 10.1080/14772000.2016.1271059 [Google Scholar]
- Soberón, J. , & Nakamura, M. (2009). Niches and distributional areas: Concepts, methods, and assumptions. Proceedings of the National Academy of Sciences of the United States of America, 106, 19644–19650. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Spagnuolo, V. , Terracciano, S. , Puglisi, M. , & Privitera, M. (2014). The taxonomic status of Campylopus pilifer subsp. vaporarius and its relationships within Campylopus Brid. (Dicranaceae, Bryophyta). Nova Hedwigia, 99, 501–510. [Google Scholar]
- Sparrius, L. B. , & Kooijman, A. M. (2011). Invasiveness of Campylopus introflexus in drift sands depends on nitrogen deposition and soil organic matter. Applied Vegetation Science, 14, 221–229. [Google Scholar]
- Sparrius, L. B. , Sevink, J. , & Kooijman, A. M. (2012). Effects of nitrogen deposition on soil and vegetation in primary succession stages in inland drift sands. Plant and Soil, 252, 261–272. [Google Scholar]
- Stamatakis, A. (2014). RAxML version 8: A tool for phylogenetic analysis and post‐analysis of large phylogenies. Bioinformatics, 30, 1312–1313. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Stech, M. (2004). Supraspecific circumscription and classification of Campylopus (Dicranaceae, Bryopsida) based on inferences from sequence data. Systematic Botany, 29, 817–824. [Google Scholar]
- Stech, M. , & Dohrmann, J. (2004). Molecular relationships and biogeography of two Gondwanan Campylopus species, C. pilifer and C. introflexus (Dicranaceae) In Goffinet B., Hollowell V., & Magill R. (Eds.), Molecular systematics of bryophytes. Monogr. Syst. Bot. Missouri Bot. Gard. 98: 415–431. [Google Scholar]
- Stech, M. , & Quandt, D. (2010). 20,000 species and five key markers: The status of molecular bryophyte phylogenetics. Phytotaxa, 9, 196–228. [Google Scholar]
- Stech, M. , Sim‐Sim, M. , & Kruijer, J. D. (2010). Campylopus Brid. (Leucobryaceae) in Macaronesia revisited. Tropical Bryology, 31, 154–163. [Google Scholar]
- Stech, M. , Veldman, S. , Larraín, J. , Muñoz, J. , Quandt, D. , Hassel, K. , & Kruijer, J. D. (2013). Molecular species delimitation in the Racomitrium canescens complex (Grimmiaceae) and implications for DNA barcoding of species complexes in mosses. PLoS ONE, 8(1), e53134 https://doi.org/10.1371/journal.pone.0053134 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Stech, M. , & Wagner, D. (2005). Molecular relationships, biogeography, and evolution of Gondwanan Campylopus species (Dicranaceae, Bryopsida). Taxon, 54, 377–382. [Google Scholar]
- Størmer, P. (1958). Some mosses from the phytogeographical excursion through the Armorican massive in 1954. Revue Bryologique et Lichenologique, 27, 13–16. [Google Scholar]
- Warren, D. L. , Glor, R. E. , & Turelli, M. (2008). Environmental niche equivalency versus conservatism: Quantitative approaches to niche evolution. Evolution, 62, 2868–2883. [DOI] [PubMed] [Google Scholar]
- Warren, D. L. , Glor, R. E. , & Turelli, M. (2010). ENMTools: A toolbox for comparative studies of environmental niche models. Ecography, 33, 607–611. [Google Scholar]
- Wiens, J. J. , Ackerly, D. D. , Allen, A. P. , Anacker, B. L. , Buckley, L. B. , Cornell, H. V. , … Stephens, P. R. (2010). Niche conservatism as an emerging principle in ecology and conservation biology. Ecology Letters, 13, 1310–1324. [DOI] [PubMed] [Google Scholar]
