Abstract
Given the high degrees of adaptation to specific microhabitats and restricted-range endemism, Goniurosaurus (Tiger geckos) serves as a unique model to study the complex evolution in lizards. Using phylogenetic analyses, we estimated the first divergence date of Goniurosaurus to the Eocene (~ 45.3 mya). The diversification within four monophyletic species groups began in the mid-Miocene between ~ 13.4 and 7.7 mya and continued to at least the early Pleistocene (~ 2 mya). Their ancestor was predicted to originate somewhere in contiguous continental Eastern Asia, whereas the current regions in which each monophyletic Goniurosaurus species group radiated are respectively their own ancestral regions. Together with factors of altitudinal gradient and climate conditions, we reconstructed relevant niche models of Goniurosaurus including ancestral reconstructions. Consequently, low elevations were predicted to be the most probable ancestral state for Goniurosaurus and all its groups as well. Both climatic niche conservatism and divergence have shaped the extraordinary species richness of allopatric Chinese and Vietnamese tiger geckos. In terms of endangerment, Goniurosaurus has been considered one of the most susceptible lizard groups under severe human impacts, especially climate change. The assessments of their niche evolution can provide a science-based pre-signal of vulnerability, thereby improving the efficacy of conservation measures to safeguard species of Goniurosaurus in the future. Accordingly, almost all closely related species of Goniurosaurus in China and Vietnam were identified with a high rate of niche conservatism, which should be included in conservation priorities under potential impacts of climate change.
Similar content being viewed by others
Avoid common mistakes on your manuscript.
Introduction
It has been acknowledged that ecological conditions are the major factors that determine the distribution of species as well as being the main driver of speciation (Darwin and Wallace 1858; MacArthur 1984; Orr and Smith 1998; Schluter 2009; Glor and Warren 2011). In particular, the largest geographic range in which a species can sustain a stable population size, is frequently limited by its physiological tolerances to ecological factors defined by its fundamental niche (Grinnell 1917; Kearney and Porter 2004). Together with biotic interactions, dispersal barriers and chance events, species actually occupy only fractions of their fundamental niche, termed realized niche that can explain the high diversity of complex range-restricted species, especially in reptile groups distributed in the tropics (Hutchinson 1957; Sterling et al. 2006; Heaney 2007; Mittelbach et al. 2007; Soberón 2007; Böhm et al. 2013; Stein et al. 2014; Steinbauer et al. 2016). In endangerment concerns, such reptiles are at high risk of extinction, following Criterion B and D2 in the IUCN Red List relative to restricted geographic range (Böhm et al. 2013; IUCN 2021). Against the background of increasing anthropogenic impacts, their survival fate is severely imperiled (Thuiller et al. 2005; Ohlemüller et al. 2008; Böhm et al. 2013; Cahill et al. 2013; Trew and Maclean 2021; Cox et al. 2022). Consequently, ecological alternations (e.g., climate change) have been globally acknowledged to be a looming factor of extinction, rather than being a driver of speciation in the past (Thuiller et al. 2005; Schluter 2009; Lavergne et al. 2013; Bellard et al. 2014; Smith et al. 2019).
Given the potential for niche evolution, the level of adaptability in a species to different environmental conditions can be estimated to assess its chances of survival. Accordingly, natural populations could be subjected to ecology-based divergent selection across the landscape under different abiotic factors (e.g. climate) as non-physical barriers favoring reproductive isolation and consequent speciation in new habitats by accumulating genetic difference (niche divergence). Consequently, the evolved lineages were detected with distinct evolutionary responses from their ancestor and a high level of physiological tolerances to niche alternations (Ahmadzadeh et al. 2013; Krehnwinkel et al. 2015; Rato et al. 2015; Ahmadi et al. 2021). On the other hand, closely related taxa tend to occupy more similar niches than distant phylogenetic congeners and retain ancestral niches over time (niche conservatism), when their speciation was mainly related to the allopatric distribution patterns by variance. Such species may be more susceptible to climate change due to constraints in genetic variation caused by previous niche conservatism limiting the likelihood of adaptation to changing conditions. Therefore, the looming threat containing novel conditions may exceed their narrower physiological tolerance, consequently leading to extirpation (Wiens and Graham 2005; Hadly et al. 2009; Wiens et al. 2010; Peterson 2011; Lavergne et al. 2013; Pyron et al. 2014; Ahmadi et al. 2021). Understanding the potential for niche evolution is particularly important in evaluating the status of endangered species and thereby proposing science-based measures of conservation (Richardson and Whittaker 2010; Wiens et al. 2010; Moritz and Potter 2013). Recently, species distribution models (SDM) have been employed to identify patterns and mechanisms of niche evolution, enabling researchers to test causal relationships between ecological traits and diversification processes (Evans et al. 2009; Hof et al. 2010; Salamin et al. 2010; Broennimann et al. 2012; Lavergne et al. 2013; Rato et al. 2015; Ahmadi et al. 2021).
Due to the high degrees of adaptation to specific microhabitats and restricted-range endemism, tiger geckos belonging to the genus Goniurosaurus Barbour, 1908 can serve as a unique model to study the complexity of evolution in lizards (Honda et al. 2014; Liang et al. 2018; Ngo et al. 2021b; Grismer et al. 2021). Recently, systematic issues of Goniurosaurus were resolved and ongoing discoveries of new species have been updated based on integrative taxonomic approaches using morphology and phylogenetics (Liang et al. 2018; Grismer et al. 2021; Ngo et al. 2021b; Zhu et al. 2022). In particular, 25 tiger geckos have been assigned to one of four monophyletic species groups: the kuroiwae group with six exclusively insular species from the Ryukyu Archipelago, Japan; the lichtenfelderi group with five species and the luii group with nine species (whereof G. kadoorieorum is recently considered a synonym of G. luii) distributed throughout insular and mainland sites in China and Vietnam; and the yingdeensis group with five continental species in southern China (Fig. 1) (Nguyen et al. 2009; Nguyen 2011; Liang et al. 2018; Qi et al. 2020; Zhu et al. 2020a, 2020b, 2021; Grismer et al. 2021; Ngo et al. 2021b, 2022a, b, c). Although most of their distributions are adjacent to each other, none of them have been recorded to be in sympatry (Orlov et al. 2008; Yang and Chan 2015; Zhu et al. 2020a, b, 2021; Ngo et al. 2021b). Oceanic archipelagos and disjunct karst ecosystems could serve as physical barriers and/or provide unique microclimate zones that might impede dispersal and hence gene flow among the Goniurosaurus populations (Clements et al. 2006; Sterling et al. 2006; Heaney 2007). Research presented by Liang et al. (2018) indeed underlined the central role of Hainan Island, which formulated species diversification within the lichtenfelderi group. Using an analysis of ancestral habitat reconstruction, Grismer et al. (2021) shed light on the evolution of habitat preference in Goniurosaurus. Accordingly, karstic ecosystems were highly supported as the most probable ancestral condition for Goniurosaurus as well as for three of the four species groups (e.g. kuroiwae, luii and yingdeensis), whereas the lichtenfelderi group most likely evolved in non-karstic habitats.
Goniurosaurus is considered one of the most threatened genera under ongoing severe human impacts (e.g. unsustainable exploitation and habitat loss) (Ngo et al. 2019). Furthermore, as highly endemic ectotherms with limited dispersal capacity, potential factors—including small population size, stochastic events and climate change can also push Goniurosaurus species to the brink of extinction (Ngo et al. 2019, 2021a, b, 2022a, b). To safeguard their populations, legal regulations listing all Tiger gecko species in CITES (Convention on International Trade in Endangered Species of Wild Fauna and Flora) appendices have recently come into force (Ngo et al. 2019; CITES Notification No. 2020/068), whereof 17 species have been considered threatened in the IUCN Red List (IUCN 2021). In spite of a wealth of studies on systematics, as well as assessments of demography and ecology (Liang et al. 2018; Ngo et al. 2019, 2021a, b, 2022a, b; Grismer et al. 2021), understanding of the potential of niche evolution in Goniurosaurus remains to be investigated in order to identify priorities in species conservation planning.
Following evolutionary hypotheses, cladogenesis in Goniurosaurus species from Eastern Asia was assumed to be strongly related to past orogenic processes that facilitated the geographic separation (e.g., disjunct limestone habitats, islands, rivers) which consequently led to reproductive isolation (Honda et al. 2014; Liang et al. 2018; Ngo et al. 2021b, 2022b). However, the simple vicariance might play only an indirect role and cannot fully explain the mechanism of speciation within Goniurosaurus. Combining a dated phylogenetic tree of all Goniurosaurus species together with their distribution data, altitudinal gradient and sets of climate conditions, we herein test evolutionary models that may explain their extraordinary richness in allopatry and high levels of endemism. In terms of species conservation planning, we also intend to identify closely related species of Goniurosaurus preserving climatic conditions over time (niche conservatism), that allows us to include them in priorities of conservation protection due to the particular vulnerability to climate change in the future.
Materials and methods
Genetic data and estimation of divergence times
Genomic DNA was extracted from muscle tissue samples, using a DNA extraction kit from Tiangen Biotech (Beijing) Co., Ltd. Primers used for 16S were r16S-5L (5′-GGTMMYGCCTGCCCAGTG-3′) and 16sbr-H (5′-CCGGTCTGAACTCAGATCACGT-3′) (Palumbi et al. 1991), for cytb the primers were L14731 (5′-TGGTCTGAAAAACCATTGTTG-3′) (Honda et al. 2014) and H15149m (5′-GCMCCTCAGAAKGATATTTGYCCTCA-3′) (Chambers and MacAvoy 1999), for CMOS the primers were FU-F (5′-TTTGGTTCKGTCTACAAGGCTAC-3′) and FU-R (5′-AGGGAACATCCAAAGTCTCCAAT-3′) (Gamble et al. 2008), and for RAG1 the primers were R13 (5′-TCTGAATGGAAATTCAAGCTGTT-3′) and R18 (5’-GATGCTGCCTCGGTCGGCCACCTTT-3′) (Groth and Barrowclough 1999). The PCR procedure was performed with an initial denaturation at 94 °C for 5 min, 35 cycles of 94 °C for 30 s, 55 °C for 30 s and 72 °C for 1 min, followed by a final extension at 72 °C for 10 min (Liang et al. 2018). PCR products were purified with spin columns and then sequenced with forward primers using BigDye Terminator Cycle Sequencing Kit as per the guidelines on an ABI Prism 3730 automated DNA sequencer by Shanghai Majorbio Bio-pharm Technology Co., Ltd.
We constructed Maximum Likelihood (ML), Bayesian Inference (BI), and Bayesian Evolutionary Analysis by Sampling Trees (BEAST) phylogenetic trees using a concatenated data set composed of 3070 base pairs (bp) of the mitochondrial genes, 16 s (633 bp) and cytb (1075 bp), and the nuclear genes, CMOS (472 bp) and RAG1 (890 bp), from 103 specimens of 24 species of Goniurosaurus with varying degrees of sequence coverage across the samples. Concatenation followed the comparison of separate gene trees to confirm there were no major discordances. One species, Eublepharis macularius, served as the outgroup (Grismer 1988; Jonniaux and Kumazawa 2008) to root all trees. See Grismer et al. (2021) for all sequence data and GenBank accession numbers.
A Maximum likelihood (ML) analysis partitioned by gene was implemented using the IQ-TREE webserver (Nguyen et al. 2015; Trifinopoulos et al. 2016) preceded by the selection of substitution models using TIM2 + F + I + G4 for 16 s and cytb and HKY + F for CMOS and RAG1. To avoid over parameterization, protein coding genes were not partitioned by codon. One-thousand bootstrap pseudo-replicates via the ultrafast bootstrap (UFB: Hoang et al. 2018) approximation algorithm were employed, and nodes having UFB values of 95 and above were considered strongly supported (Minh et al. 2013). We considered nodes with values of 90–94 as well-supported. A Bayesian inference (BI) analysis was carried out in MrBayes 3.2.3. (Ronquist et al. 2012) on XSEDE using the CIPRES Science Gateway (Cyberinfrastructure for Phylogenetic Research; Miller et al. 2010) employing default priors and models of evolution that most closely approximated those selected by the BIC and used in the ML analysis. Two independent Markov chain Monte Carlo (MCMC) analyses for each data set were performed—each with four chains, three hot and one cold. The MCMC simulations ran for 100 million generations. Trees were sampled every 10,000 generations, and the first 10% of the trees from each run from each data set were discarded as burn-in. The parameter files from both runs were checked in Tracer v1.6 (Rambaut et al. 2014) to ensure that convergence and stationarity of all parameters had effective sample sizes (ESS) well-above above 200. Post-burn-in sampled trees from each respective run were combined and 50% majority-rule consensus trees were constructed. Nodes with Bayesian posterior probabilities (BPP) of 0.95 and above were considered highly supported. We considered nodes with values of 0.90–0.94 as well-supported.
An input file was constructed in Bayesian Evolutionary Analysis Utility (BEAUti) v. 2.4.6 using a relaxed lognormal clock with unlinked site models, linked trees and clock models, and a Yule prior and run in BEAST on CIPRES (Cyberinfrastructure for Phylogenetic Research; Miller et al. 2010). bModelTest was used to numerically integrate over the uncertainty of substitution models of each gene while simultaneously estimating phylogeny using MCMC analyses. MCMC chains were run for 100,000,000 generations and logged every 10,000 generations. The BEAST log file was visualized in Tracer v. 1.6.0 (Rambaut et al. 2014) to ensure effective sample sizes (ESS) were well-above 200 for all parameters. A Maximum clade credibility tree using mean heights at the nodes was generated using TreeAnnotator v.1.8.0 (Rambaut and Drummond 2014) with a burn-in of 1000 trees (10%). Nodes with BPPs of 0.95 and above were considered strongly supported. We considered nodes with values of 0.90–0.94 as well-supported.
Ancestral range estimation
The resulting BEAST tree was used to estimate the ancestral range at each node using the R package BioGeoBEARS (Matzke 2014). We followed the dating scheme of Jonniaux and Kumazawa (2008) in order to compare it with the BEAST and treePL (Smith and O’Meara 2012) analyses of divergence times of Liang et al. (2018). BioGeoBEARS allows for both probabilistic inferences of ancestral geographic ranges and statistical comparisons of range expansion from different models in a likelihood framework employing the Akaike Information Criterion (AIC) to allow the data to choose the best fitting model. Available models in BioGeoBEARS include a likelihood version of the parsimony-based Dispersal Vicariance Analysis DIVA (“DIVALIKE”) (Ronquist 1997), the likelihood-based Dispersal-Extinction Cladogenesis (DEC) model of the LAGRANGE program (Ree and Smith 2008), and the Bayesian-based BayArea (“BAYAREALIKE”) (Landis et al. 2013). Additionally, each model incorporates founder-effect speciation (+ J) which is purported to be particularly important when reconstructing biogeographic scenarios of insular lineages (Matzke 2014). For a geography input file, we classified Goniurosaurus species into distinct areas of the four monophyletic groups’ current geography following the division of Liang et al. (2018), including (1) Guangdong Province, China (C) with four species of yingdeensis group (Qi et al. 2020); (2) Hainan Island, China (H) with four species of lichtenfelderi group (except for G. lichtenfelderi); (3) Ryukyu Archipelago, Japan (R) with six species of kuroiwae group; and (4) Vietnam and China (V) from Red River fault in northern Vietnam, northward to southern Guizhou Province, China, with nine species of luii group and G. lichtenfelderi. Each species occurs in only a single region and as such was allowed to assign only a single selected area in the analysis (Liang et al. 2018; Grismer et al. 2021; Ngo et al. 2021b).
Occurrence records
A total of 223 occurrence records of 16 Goniurosaurus species in China and Vietnam were collected from our field surveys during the two last decades by ourselves and others (Fig. 1). In order to improve the quality of predictions based on our models, which may be affected by geographic bias as results of duplicates representing pseudo replicates, we randomly selected only one record within each 1 km square by using spatial filtering functions in R v 3.1.2 (RStudio Team 2018; Aiello-Lammens et al. 2015). Consequently, 160 representative records of three Goniurosaurus species groups (including lichtenfelderi—44 records, luii—79 records and yingdeensis—38 records, see details in Supplementary information Table S1) were used for further analyses.
Ancestral elevational range reconstruction
Based on significant changes of vegetation as Bain and Hurley (2011) suggested for the study area, the elevational ranges were divided into three different levels, namely low (below 300 m), medium (310–800 m) and high (above 800 m). The coding of elevation level for each Goniurosaurus species, which was determined from the literature and field observations of the authors, was extracted from coordinate data of occurrences using GPS equipment (Supplementary Information Fig. S1). The classification was mapped onto the BEAST tree of Goniurosaurus using a stochastic character mapping (SCM) implemented in the R package phytools (Revell 2012) in order to derive probability estimates of the ancestral states at each node. A transition rate matrix was identified that best fit the data by comparing the corrected Akaike Information Criterion (AICc) in the R package ape (Paradis and Schliep 2018). Three transition rate models were considered: a 2-parameter model having different rates for every transition type (the ARD model); a single-parameter model with equal forward and reverse rates between states (the symmetrical rates SYM model); and a single rate parameter model that assumes equal rates among all transitions (ER). Lastly, an MCMC approach was used to sample the most probable 1000 trait histories from the posterior using the make.simmap() command and then summarized them using the summary() command.
Climatic niche comparisons
In terms of environmental data, 19 bioclimatic variables for current conditions with a spatial resolution of 30 arc-second were obtained from Worldclim (http://www.worldclim.org/, version 2.0) (Fick and Hijmans 2017). To mitigate the influence of potential multicollinearity of predictors on the models, we computed a pairwise Pearson correlations to identify and eliminate highly correlated climatic variables with r coefficient values larger than │0.7│ (Dormann et al. 2013). Our final data set comprised seven climatic variables including Mean Diurnal Range (BIO2), Isothermality (BIO3), Max Temperature of Warmest Month (BIO5), Mean Temperature of Wettest Quarter (BIO8), Precipitation of Wettest Month (BIO13), of Driest Month (BIO14) and Warmest Quarter (BIO18), which were selected for subsequent analyses.
To compare the macro-climatic niche among Goniurosaurus groups and sister taxa of each group, all pairwise tests were computed by using the package “ecospat” in R software (Cola et al. 2017). The niche equivalency and two-way similarity tests, presented in detail by Warren et al. (2008) and Broennimann et al. (2012), were calculated between pairs of Goniurosaurus groups. The degree of overlap in climatic-niche space was further evaluated using Schoener’s D as recommended by Rödder and Engler (2011), which varies from 0 (no overlap) to 1 (complete overlap) (Schoener 1970; Warren et al. 2008). However, the niche overlap indices among species-pairs cannot be reliably estimated due to the limited availability of records with less than 10 (Rödder et al. 2011), which is the case in most Tiger geckos. Following a jackknifing approach proposed by Rödder et al. (2011) to overcome the limitation, all available Goniurosaurus records of each monophyletic group were pooled into a dataset and then repeated “leave-one-species-out” to calculate Schoener’s D values. We subsequently used the value of 1-D as the relative degree of overlap between the omitted one and all remaining species.
Each macro-climatic niche was described in an orthogonal space combining the first two principal components in the PCA-env approach (Broennimann et al. 2012). The overlap level of given macro-climatic niche spaces was evaluated by direct observations on the same environmental background. The proportion of each principal component (PC) explaining climatic variance was calculated by the proportion of its eigenvalue to the sum. To define the available macro-climatic space, we constructed a minimum convex polygon (MCP) covering a total of selected Goniurosaurus records using the package “adehabitatHR” in R software (Calenge 2006).
Species distribution modelling
For species for which only one or two occurrence records were available (namely G. araneus, G. gezhi, G. liboensis, G. kwangsiensis, G. kadoorieorum, G. gollum and G. zhoui), we estimated their potential distributions by applying a circular buffer with a radius of 10 km around occurrence points with dissolved boundaries in R. In terms of SDM, the potential distributions of remaining tiger geckos were predicted by using the ensemble of small models (ESMs) combining six modelling techniques: artificial neural network (ANN), classification tree analysis (CTA), generalized linear models (GLM), generalized additive models (GAM), generalized boosting regression models (GBM), and maximum entropy modelling (MAXENT.Phillips). All models were calibrated using the “biomod2” package (Breiner et al. 2015; Thuilleret et al. 2016; Cola et al. 2017). Based on the seven selected climatic variables, we computed a principal component analysis (PCA) in R to derive an orthogonal niche space. Only principal components (PCs) with eigenvalues > 1 were subsequently considered, which were subsequently employed in the SDM (Rato et al. 2015). Although the potential distribution of each species was projected within the entire background, all models were only trained with presence-only data and 10,000 random points selected within the MCP area. Subsets of 70% training data and 30% test data were used to model and evaluate the SDMs using the two performance indices AUC and TSS (Fielding and Bell 1997; Allouche et al. 2006). Values closer to 1.0 indicate better model performance (Breiner et al. 2015).
History of niche occupancy
Following an approach proposed by Evans et al. (2009), the evolutionary history of climatic niche occupancy of Goniurosaurus species in China and Vietnam was reconstructed throughout predicted niche occupancy (PNO) profiles in the “phyloclim” package. The suitable probability derived from ESMs of each Goniurosaurus species was re-scaled to the sum of 1, and corresponding PC scores binned into 1000 grid cells together with designed ones of occurrence-limited species in order to obtain the PNO profile for each PC. From these PNO profiles, we resampled 1000 times using the generalized least squares method with an assumption of Brownian motion evolution to estimate the climatic spectrum on the BEAST dated tree of Goniurosaurus species in China and Vietnam (Rato et al. 2015; Ahmadzadeh et al. 2016; Ahmadi et al. 2021).
Ancestral climatic state estimation
We tested for phylogenetic signals in climatic niche axes based on climatic PCs and our dated phylogenetic tree, using Blomberg’s K (Blomberg et al. 2003) and Moran’s I (Münkemüller et al. 2012) in the “phylosig” function of the package “phytools” in R. A phylogenetic signal was identified with a significance level of p < 0.05, indicating that Blomberg’s K and Moran’s I are significantly different from zero. In particular, values of K range from zero to infinity, where K < 1 indicates weak phylogenetic signal, and K > 1 strong signal, implying that sister taxa are, respectively, more or less divergent in environmental traits. In terms of Moran’s I, the value reaches to + 1 indicating a perfect cluster of similar traits, whereas the value of − 1 indicates the highest autocorrelation of dissimilar traits.
We illustrated the ancestral state of climatic PCs to assess the pattern of climatic evolution of Tiger geckos by using the “contMap” function of the “phytools” package in R software (Revell 2012, 2013). For climatic input data, we averaged the climatic spectrum of each climatic PC from the PNO profiles for each Tiger gecko. The best model to describe trait evolution was ranked based on the AICs tests for four commonly proposed models: Brownian motion (BM), Ornstein–Uhlenbeck (OU), Early Burst (EB) and Lambda, using the “fitContinuous” function of “geiger” package (Pennell et al. 2014). We computed the maximum likelihood (ML) to predict the climatic state following the equation from Felsenstein (1985).
Results
Phylogenetic relationships and divergence dating
The time-calibrated BEAST analysis recovered a phylogeny with well-supported nodes (BPP ≥ 90) throughout the tree (Fig. 2). The divergence dates are similar to those calculated by Liang et al. (2018) and fall well within the range of their calculated highest posterior density (HPD).
Based on our dated phylogeny, the first divergence of Goniurosaurus was estimated to happen during the Eocene at approximately ~ 45.3 mya and the radiation continued across East Asia up until the Pliocene. Diversification within four monophyletic species groups began in the mid-Miocene between ~ 13.4 and 7.7 mya (million years ago) and continued to at least the early Pleistocene ~ 2 mya (Fig. 2).
Ancestral reconstruction of geographical ranges and elevation
The BioGeoBEARS model indicated that the DEC + J model recovered the best fit to the data and most likely to infer the correct ancestral range at each node being that it had the lowest AIC-wt score (Supplementary Information Table S2). The range analyses estimated that the respective ancestral regions for each group are the same regions in which each group currently inhabits. Liang et al. (2018) considered this to be a recent dispersal event. However, the geographical origin of Goniurosaurus is not clearly specified. The analysis indicated that all the deep nodes outside those of the species groups, recovered an essentially equal probability that Goniurosaurus originated anywhere across the combined areas. Given the young age and relatively recent geographic isolation of the Ryukyu Archipelago and Hainan Island from the late Mioence (Sterling et al. 2006; Honda et al. 2014; Liang et al. 2018), as for now, we assume that the Goniurosaurus evolved in continental East Asia. With additional fieldwork and the potential discovery of new species in the north of Guangdong Province, the region of origin could be further refined.
History of altitudinal transitions
All Goniurosaurus species have been recorded in areas ranging from 40 to 1000 m elv (Supplementary Information Fig. S1). The AIC scores for the three transition models were ARD = 47.0085, SYM = 43.60873, and ER = 40.07807. The SCM using the best ER model predicted that the “low” level is the most probable ancestral state at the crown tree and all group nodes, except for the “high” level at the common node of three lineages (namely G. kwanghua, G. hainanensis, G. lichtenfelderi) (Fig. 3).
Niche overlap comparison
Climatic niche spaces of three Goniurosaurus groups in China and Vietnam were illustrated in the PCA-env analysis and its first two dimensions accounted for 65.5% of overall variance in the climatic data set (whereof, PC1: 38.6%—explained by Mean Diurnal Range (BIO2), Precipitation of Driest Month (BIO14) and Warmest Quarter (BIO18); and PC2: 26.9%—related by Isothermality (BIO3), Max Temperature of Warmest Month (BIO5), Mean Temperature of Wettest Quarter (BIO8), Precipitation of Wettest Month (BIO13)) (Fig. 4). The analysis revealed no overlaps among their climatic spaces, especially the niche space of the yingdeensis group which is entirely separated from the remaining groups (Fig. 4). The niche overlap between group-pairs in terms of Schoener’s D only ranges from nearly 0 (yingdeensis and two remaining groups) to very limited overlap with D = 0.15 (lichtenfelderi and luii groups). Furthermore, the climatic spaces occupied by the three groups were neither significantly similar (p > 0.05) nor equivalent (p = 1.00) in all group-pair comparisons (Supplementary Information Fig. S2, Table S3).
The Jackknifing approaches omitting records of each species from the pooled data of each group documented low “Schoener’s D”—high “1-D” values in some cases, including G. lichtenfelderi (1-D = 0.998) omitted from the lichtenfelderi group, G. catbaensis (0.844) and G. liboensis (0.418) from the luii group, and G. varius (0.61) from the yingdeensis group (Table 1). Our results of the PCA-env analysis further noted in these cases that the niche space of each group shrunk significantly (Supplementary Information Fig. S3).
History of climatic evolution
The first four climatic PCs from the PCA analysis for SDM account for 90% of overall climatic variance, whereof PC1: 39.3% was mainly associated with Mean Temperature of Wettest Quarter (BIO8), PC2: 23.9% with Precipitation of Driest Month (BIO14), PC3: 18.1% with Max Temperature of Warmest Month (BIO5) and PC4: 7.8% with Isothermality (BIO3). These PCs variables were employed together with geographic records for the SDMs. The indices of TSS and AUC indicated that the fitted EP-ESMs of nine selected Tiger geckos performed well (Supplementary Information Fig. S4). Using the results of climatic niche models for the potential distribution and circling suitable sites of remaining species (Supplementary Information Fig. S5), we reconstructed on the BEAST dated tree the ancestral niche occupancy profiles of Chinese–Vietnamese Goniurosaurus species, which presented only the niche evolution pattern of divergence in given Goniurosaurus groups and intermixed with the conservatism pattern among their lineages (Supplementary Information Fig. S5).
Phylogenetic signals in climatic variables were only detected in PC1 and PC4 (p-values ≤ 0.05), but these signals were relatively low according to Blomberg’s K values, being < 1 and Moran’s I values only reached 0.16 (Supplementary Information Table S4). The AICc test suggested the Brownian Motion (BM) model was the most likely scenario (Supplementary Information Table S4). Consequently, the ancestral state estimation also recovered a mix of both climatic patterns (Fig. 6). In particular, the pattern of divergence was documented among three Goniurosaurus groups in PC4 and PC2, and between the yingdeensis group and two remaining groups in PC1 and PC3. Given among their lineages, almost Goniurosaurus species followed a conservative pattern, except for G. lichtenfelderi of the lichtenfelderi group in four PC variables, and G. catbaensis in the first three PCs, G. kwangsiensis in PC2 and PC3 and G. liboensis in PC1 of luii group (Figs. 5, 6).
Discussion
Evolution
Given estimations of the ancestral range in this study and Liang et al. (2018), the origin of the ancestral range of Goniurosaurus was predicted to be somewhere in continental Eastern Asia, including the Ryukyu Archipelago and Hainan Island prior to the Eocene, as opposed to a specified location. On the other hand, our analyses revealed that the current regions in which each monophyletic Goniurosaurus group radiated, are respectively their own ancestral region of origin. Dispersals of populations of insular groups (namely kuroiwae and lichtenfelderi) were therefore considered related to prior tectonic events following the late Paleocene, such as the collision of India and Eurasia and the clockwise rotation of the Philippine Sea plate (Seno et al. 1993; Ota 1998; Teng and Lin 2004; Sterling et al. 2006; Liang et al. 2018). Subsequent seaways served as a dispersal barrier that prevented gene flow among populations. Therefore, vicariant evolution resulted in the formation of the two insular groups (~ late Mioence). The collision also established the land bridge accounting for the presence of colonized Indian populations of the Draconinae subfamily from Eurasian ancestors during the early to late Eocene (Grismer et al. 2021).
We used ecological niche models to elucidate the role of the Grinnellian niche (e.g., climate conditions) in the diversification of Goniurosaurus in China and Vietnam. Accordingly, the niche divergence in all PCs based on climatic variables was strongly correlated with the formation of the yindeensis group by the middle Oligocene (Figs. 4, 5, 6). On the other hand, the dominant climate of the tropical monsoon toward southeastern China and northern Vietnam was caused by the uplift of Tibetan Plateau as a result of India’s collision with Eurasia as well (Sterling et al. 2006; Miao et al. 2013). The subsequent envelopment of monsoon tropical conditions since the Oligocene, might have also driven the cladogenesis of the two remaining groups (e.g., lichtenfelderi and luii). In particular, we documented the very low overlap between their niche spaces in the PCA-env analysis (Fig. 4) and the discordance in their climatic spectrums (e.g., PC2 and PC4) in the PNO estimation (Figs. 5, 6). Furthermore, Grismer et al. (2021) estimated that karst ecosystems are the most probable ancestral habitat for most Goniurosaurus groups, except for the lichtenfelderi group which mostly inhabits non-karst environments (Grismer et al. 2021).
Hainan Island is strongly supported as the ancestral range of the lichtenfelderi group (Liang et al. 2018). A mixture of karst and granite formations on Hainan Island that may have promoted the phylogenetic split between G. bawanglingensis and the most recent common ancestor of G. zhoui and G. kwanghua, following the evolution of habitat preference (Liang et al. 2018; Grismer et al. 2021). The emergence of other species within the lichtenfelderi group might generally be associated with climatic cycles during the Pliocene and early Pleistocene (Herzschuh et al. 2016). Accordingly, low-to-high transitions along the elevation gradient toward highland refugia on Hainan Island occurred during the interglacial mid-Pliocene, and thereby tiger geckos (the common ancestor of G. kwanghua, G. hainanensis and G. lichtenfelderi) avoided much warmer climatic conditions. The latest speciation event between G. hainanensis and G. lichtenfelderi in non-karst habitats during the early Pleistocene might relate to altitudinal partitioning as well, but vice versa. In particular, the Hainan populations of Goniurosaurus dispersed overwater or overland to occupy low elevations in the Vietnamese mainland during sequential glacial periods of sea level decline (Li et al. 2010; Herzschuh et al. 2016; Liang et al. 2018). Following a pattern of vicariance, these populations were gradually isolated by increasing the sea levels, and eventually evolved into G. lichtenfelderi (~ 2 mya) at both island and mainland sites in Vietnam.
Besides the ocean serving as barrier, the latest speciation event in the lichtenfelderi group is also supported by the non-physical barrier of climatic niche limits. We documented the pattern of niche divergence in all selected climatic conditions between G. lichtenfelderi and Hainan populations of Goniurosaurus (Figs. 5, 6). The role of Grinnellian niche in cladogenetic processes was further assessed in other groups of Goniurosaurus. In general, the low phylogenetic signals within Goniurosaurus were strongly influenced by various climate spectra in the luii group. In particular, three Goniurosaurus species of the luii group followed the pattern of climatic divergence, including G. catbaensis in most climatic conditions (except for Isothermality of PC4), G. kwangsiensis in Precipitation of Driest Month (PC2) and Max Temperature of Warmest Month (PC3), and G. liboensis in Mean Temperature of Wettest Quarter (PC1) (Figs. 5, 6). On the other hand, the remaining species in the luii group and all species in the yingdeensis group adapted to their convergent gradients of all climatic conditions, representing a high degree of niche conservatism (Figs. 5, 6). Accordingly, the radiation of their common ancestors in Vietnam and China mainland might be enveloped within homogenous niche spaces. The subsequent speciation events among these populations of Goniurosaurus might be related to potential barriers created by disjunct karst ecosystems, and/ or large rivers or canyons offering various micro-niches (Clements et al. 2006; Chen et al. 2014; Qi et al. 2020; Grismer et al. 2021; Ngo et al. 2021b, 2022b; Zhu et al. 2021). For example, the Zuojiang and Ky Cung rivers might establish an eastern boundary between G. luii and G. araneus in China and G. huuliensis in Vietnam, respectively (Ngo et al. 2022b). Given a case of uncertain taxonomy in Goniurosaurus, the high level of niche conservatism agreed well with the morphological and genetic similarities between G. kadoorieorum and G. luii, confirming the junior synonym status as proposed by Grismer et al. (2021) and Ngo et al. (2021b).
Conservation
Due to high degrees of endemism and small population sizes, all species of Goniurosaurus are particularly vulnerable to human impacts (Ngo et al. 2019, 2022b, c; Grismer et al. 2021). In this study, our results suggest that the closely related species within the yingdeensis group, the lichtenfelderi group on Hainan Island and some in the luii group, show patterns of niche conservatism and hence appear to be more susceptible to climate change (Wiens and Graham. 2005; Hadly et al. 2009; Wiens et al. 2010; Peterson 2011; Lavergne et al. 2013; Pyron et al. 2014; Ahmadi et al. 2021). Their probability of survival in the future has been even reduced decisively by the loss of genetic diversity that likely occurs in most Goniurosaurus species due to population declines (e.g., over-exploitation) and habitat destruction (e.g., forest fragmentation, quarrying of limestone karst and infrastructure) (Frankham et al. 2002; Ngo et al. 2019; 2022b, c). To avoid the extinction pressure of climate change, a natural response of species are range shifts towards optimal environments (Sinervo et al. 2010). However, the range-restricted tiger geckos are unable to migrate larger distances to climatic refugia, which were forecasted to be greatest towards higher latitudes in proximity to temperate regions, due to either habitat specialization or lacking forest corridors (Williams et al. 2007; Ngo et al. 2021a, 2022a). The dense forest canopy, wide elevation gradient and complex karst formations likely construct unique micro-refugia containing favorable micro-climate conditions which could buffer species against suboptimal climates (Clements et al. 2006; Sterling et al. 2006; Ohlemüller et al. 2008; Suggitt et al. 2018). However, this last survival chance is currently getting narrower due to the intensive loss of micro-refugia as the result of deforestation and quarrying in karst formations (Clements et al. 2006; Queiroz et al. 2013; CEPF 2020; Ngo et al. 2022b, c). Therefore, higher conservation priorities and stringent protection should be immediately implemented to prevent these niche-conservative species of Goniurosaurus from entering an extinction vortex. However, this modelling-based assessment does not necessarily indicate that the remaining Goniurosaurus species can overcome environmental changes to adapt. In particular, both G. lichtenfelderi and G. catbaensis showing the pattern of niche divergence while G. huuliensis following the pattern of niche conservatism, all three of them are potentially impacted by climate change (Le et al. 2017; Ngo et al. 2021a, 2022a). Although approaches to identify the pattern of niche evolution of Goniurosaurus are necessary for conservation priorities, the species’ endangered level should be further assessed based on comprehensive biological knowledge of population status, ecological characteristics, and human impacts. The combination of biological background data is expected to significantly improve the efficacy of conservation plans and actions to safeguard the future existence of the species of Goniurosaurus.
Data availability
The data that support the findings of this study are available from the corresponding author [Hai Ngoc Ngo], upon reasonable request.
References
Ahmadi M, Hemami MR, Kaboli M, Nazarizadeh M, Malekian M, Behrooz R, Geniez P, Alroy J, Zimmermann NE (2021) The legacy of Eastern Mediterranean mountain uplifts: rapid disparity of phylogenetic niche conservatism and divergence in mountain vipers. BMC Ecol Evol 21:130. https://doi.org/10.1186/s12862-021-01863-0
Ahmadzadeh F, Flecks M, Carretero MA, Böhme W, Ilgaz C, Engler JO, Harris DJ, Üzüm N, Rödder D (2013) Rapid lizard radiation lacking niche conservatism: ecological diversification within a complex landscape. J Biogeogr 40:1475–1489. https://doi.org/10.1111/jbi.12121
Ahmadzadeh F, Flecks M, Carretero MA, Böhme W, Ihlow F, Kapli P, Miraldo A, Rödder D (2016) Separate histories in both sides of the Mediterranean: Phylogeny and niche evolution of ocellated lizards. J Biogeogr 43:1242–1253. https://doi.org/10.1111/jbi.12703
Aiello-Lammens MA, Boria RA, Radosavljevic A, Vilela B, Anderson RP (2015) spThin: an R package for spatial thinning of species occurrence records for use in ecological niche models. Ecography 38:541–545. https://doi.org/10.1111/ecog.01132
Allouche O, Tsoar A, Kadmon R (2006) Assessing the accuracy of species distribution models: prevalence, kappa and the true skill statistic (TSS). J Appl Ecol 43:1223–1232. https://doi.org/10.1111/j.1365-2664.2006.01214.x
Bain RH, Hurley MM (2011) A biogeographic synthesis of the Amphibians and Reptiles of Indochina. Bull Am Mus Nat Hist 360:138
Bellard C, Leclerc C, Leroy B, Bakkenes M, Veloz S, Thuiller W, Courchamp F (2014) Vulnerability of biodiversity hotspots to global change. Glob Ecol Biogeogr 23(12):1376–1386. https://doi.org/10.1111/GEB.12228
Blomberg SP, Garland T, Ives AR (2003) Testing for phylogenetic signal in comparative data: behavioral traits are more labile. Evolution 57:717–745. https://doi.org/10.1111/j.0014-3820.2003.tb00285.x
Böhm M, Collen B, Baillie JEM, Bowles P, Chanson J, Cox N et al (2013) The conservation status of the world’s reptiles. Biol Conserv 157:372–385. https://doi.org/10.1016/j.biocon.2012.07.015
Breiner FT, Guisan A, Bergamini A, Nobis MP (2015) Overcoming limitations of modelling rare species by using ensembles of small models. Methods Ecol Evol 6:1210–1218. https://doi.org/10.1111/2041-210X.12403
Broennimann O, Fitzpatrick MC, Pearman PB, Petitpierre B, Pellissier L, Yoccoz NG, Thuiller W, Fortin MJ, Randin C, Zimmermann NE, Graham CH, Guisan A (2012) Measuring ecological niche overlap from occurrence and spatial environmental data. Glob Ecol Biogeogr 21(4):481–497. https://doi.org/10.1111/j.1466-8238.2011.00698.x
Cahill AE, Aiello-Lammens ME, Fisher-Reid MC, Hua X, Karanewsky CJ, Yeong Ryu H, Sbeglia GC, Spagnolo F, Waldron JB, Warsi O, Wiens JJ (2013) How does climate change cause extinction? Proc R Soc Lond Ser B Biol Sci 280:20121890. https://doi.org/10.1098/rspb.2012.1890
Calenge C (2006) The package “adehabitat” for the R software: a tool for the analysis of space and habitat use by animals. Ecol Model 197:516–519. https://doi.org/10.1016/j.ecolmodel.2006.03.017
CEPF – Critical Ecosystem Partnership Fund (2020) Ecosystem profile: Indo-burma biodiversity hotspot, 2020 Update
Chambers G, MacAvoy ES (1999) Molecular genetic analysis of hybridization. Department of Conservation, Wellington, p 29
Chen TB, Meng YJ, Jiang K, Li PP, Wen BH, Lu W, Lazell J, Hou M (2014) New record of the leopard gecko Goniurosaurus araneus (Squamata: Eublepharidae) for China and habitat portioning between geographically and phylogenetically close leopard geckos. IRCF Rept Amphib 21(1):16–27. https://doi.org/10.17161/randa.v21i1.13981
Clements R, Sodhi NS, Schilthuizen M, Ng PKL (2006) Limestone karsts of Southeast Asia: imperiled arks of biodiversity. Bioscience 56:733–742. https://doi.org/10.1641/0006-3568(2006)56[733:LKOSAI]2.0.CO;2
Cola VD, Broennimann O, Petitpierre B, Breiner FT, D’Amen M, Randin C, Engler R, Pottier J, Pio D, Dubuis A, Pellissier L, Mateo RG, Hordijk W, Salamin N, Guisan A (2017) Ecospat: an R package to support spatial analyses and modeling of species niches and distributions. Ecography 40:01–14. https://doi.org/10.1111/ecog.02671
Cox N, Young BE, Bowles P et al (2022) A global reptile assessment highlights shared conservation needs of tetrapods. Nature 605(7909):285–290. https://doi.org/10.1038/s41586-022-04664-7
Darwin CR, Wallace AR (1858) On the tendency of speciesto form varieties; and on the perpetuation of varieties and speciesby natural means of selection. J Proc Linn Soc Lond Zool 3:46–50
Dormann CF, Elith J, Bacher S, Carré GCG, García Márquez JR, Gruber B, Lafourcade B, Leitao PJ, Münkemüller T, McClean CJ, Osborne PE, Reneking B, Schröder B, Skidmore AK, Zurell D, Lautenbach S (2013) Collinearity: a review of methods to deal with it and a simulation study evaluating their performance: open access. Ecography 36(1):27–46. https://doi.org/10.1111/j.1600-0587.2012.07348.x
Evans MEK, Smith SA, Flynn RS, Donoghue MJ (2009) Climate, niche evolution, and diversification of the “birdcage” evening primroses (Oenothera, Sections Anogra and Kleinia). Am Nat 173:225–240. https://doi.org/10.1111/jbi.12703
Felsenstein J (1985) Phylogenies and the comparative method. Am Nat 125(1):1–15
Fick SE, Hijmans RJ (2017) WorldClim 2: new 1km spatial resolution climate surfaces for global land areas. Int J Climatol 37(12):4302–4315. https://doi.org/10.1002/joc.5086
Fielding AH, Bell JF (1997) A review of methods for the assessment of prediction errors in conservation presence/absence models. Environ Conserv 24:38–49. https://doi.org/10.1017/S0376892997000088
Frankham R, Ballou J, Briscoe D (2002) Introduction to conservation genetics, 1st edn. Cambridge University Press, Cambridge
Glor RE, Warren D (2011) Testing ecological explanations for biogeographic boundaries. Evol Int J Org Evol 65(3):673–683. https://doi.org/10.1111/j.1558-5646.2010.01177.x
Grinnell J (1917) The niche-relationships of the California Trasher. Auk 34(4):427–433
Grismer LL (1988) The phylogeny, taxonomy, classification, and biogeography of eublepharid geckos (Reptilia: Squamata). In: Estes R, Pregill G (eds) Phylogenetic relationships of the lizard families. Stanford University Press, Stanford, pp 369–469
Grismer LL, Ngo HN, Qi S, Wang YY, Le MD, Ziegler T (2021) Phylogeny and evolution of habitat preference in Goniurosaurus (Squamata: Eublepharidae) and their correlation with karst and granite-stream-adapted ecomorphologies in species groups from Vietnam. Vertebr Zool 71:335–352. https://doi.org/10.3897/vz.71.e65969
Groth JG, Barrowclough GF (1999) Basal divergences in birds and the phylogenetic utility of the nuclear RAG-1 gene. Mol Phylogenet Evol 12:115–123
Hadly EA, Spaeth PA, Li C (2009) Niche conservatism above the species level. Proc Natl Acad Sci USA 106:19707–19714. https://doi.org/10.1073/pnas.0901648106
Heaney LR (2007) Is a new paradigm emerging for oceanic island biogeography? J Biogeogr 34:753–757. https://doi.org/10.1111/j.1365-2699.2007.01692.x
Herzschuh U, Birks HJB, Laepple T, Andreev A, Melles M, Brigham-Grette J (2016) Glacial legacies on interglacial vegetation at the Pliocene-Pleistocene transition in NE Asia. Nat Commun 7:11967. https://doi.org/10.1038/ncomms11967
Hoang DT, Chernomor O, von Haeseler A, Minh BQ, Vinh LS (2018) UFBoot2: improving the ultrafast bootstrap approximation. Mol Biol Evol 35:518–522. https://doi.org/10.1093/molbev/msx281
Hof C, Rahbek C, Araújo MB (2010) Phylogenetic signals in the climatic niches of the world’s amphibians. Ecography 33:242–250. https://doi.org/10.1111/j.1600-0587.2010.06309.x
Honda M, Kurita T, Toda M, Ota H (2014) Phylogenetic relationships, genetic divergence, historical biogeography and conservation of an endangered gecko, Goniurosaurus kuroiwae (Squamata: Eublepharidae), from the central Ryukyus, Japan. Zoolog Sci 31:309–320. https://doi.org/10.2108/zs130201
Hutchinson GE (1957) Concluding remarks. Cold Spring Harb Symp Quant Biol 22:415–427
IUCN (2021) The IUCN red list of threatened species. Version 2021-3. https://www.iucnredlist.org. Accessed 29 July 2022
Jonniaux P, Kumazawa Y (2008) Molecular phylogenetic and dating analyses using mitochondrial DNA sequences of eyelid geckos (Squamata: Eublepharidae). Gene 407:105–115. https://doi.org/10.1016/j.gene.2007.09.023
Kearney M, Porter WP (2004) Mapping the fundamental niche: physiology, climate and the distribution of a nocturnal lizard. Ecology 85(11):3119–3131. https://doi.org/10.1890/03-0820
Krehnwinkel H, Rödder D, Tautz D (2015) Eco-Genomic analysis of the poleward range expansion of the wasp spider Argiope bruennichi shows rapid adaptation and genomic admixture. Glob Change Biol 21:4320–4332. https://doi.org/10.1111/gcb.13042
Landis MJ, Matzke NJ, Moore BR, Huelsenbeck JP (2013) Bayesian analysis of biogeography when the number of areas is large. Syst Biol 62:789–804. https://doi.org/10.1093/sysbio/syt040
Lavergne S, Evans ME, Burfield IJ, Jiguet F, Thuiller W (2013) Are species’ responses to global change predicted by past niche evolution? Philos Trans R Soc Lond 368(1610):20120091. https://doi.org/10.1098/rstb.2012.0091
Le QT, Le XC, Le MH, Tran AT, Chu TH, Nguyen QT, Ngo NH (2017) Existing status and impact of climate change to the distribution of Goniurosaurus catbaensis. In: Proceedings of the 7th national scientific conference on ecology and biological resources. pp 1034–1040
Li Z, Zhang Y, Li Y, Zhao J (2010) Palynological records of Holocene monsoon change from the Gulf of Tonkin (Beibuwan), northwestern South China Sea. Quatern Res 74:8–14. https://doi.org/10.1016/j.yqres.2010.04.012
Liang B, Zhou RB, Liu YL, Chen B, Grismer LL, Wang N (2018) Renewed classification within Goniurosaurus (Squamata: Eublepharidae) uncovers the dual roles of a continental island (Hainan) in species evolution. Mol Phylogenet Evol 127:646–654. https://doi.org/10.1016/j.ympev.2018.06.011
MacArthur RH (1984) Geographical ecology. Patterns in the distribution of species. Princeton University Press, Princeton
Matzke NJ (2014) Model selection in historical biogeography reveals that founder-event speciation is a crucial process in Island clades. Syst Biol 63:951–970. https://doi.org/10.1093/sysbio/syu056
Miao Y, Wu F, Herrmann M, Yan X, Meng Q (2013) Late early Oligocene East Asian summer monsoon in the NE Tibetan Plateau: evidence from a palynological record from the Lanzhou Basin, China. J Asian Earth Sci 75:46–57. https://doi.org/10.1016/j.jseaes.2013.07.003
Miller MA, Pfeiffer W, Schwartz T (2010) Creating the CIPRES Science Gateway for inference of large phylogenetic trees. In: Proceedings of the gateway computing environments workshop (GCE), 14 Nov. 2010, New Orleans. pp 1–8. https://doi.org/10.1109/GCE.20doi: 10.5676129
Minh BQ, Nguyen MAT, von Haeseler A (2013) Ultrfast approximation for phylogenetic bootstrap. Mol Biol Evol 30:1188–1195. https://doi.org/10.1093/molbev/mst024
Mittelbach GG, Schemske DW, Cornell HV, Allen AP, Brown JM, Bush MB, Harrison SP, Hurlbert AH, Knowlton N, Lessios HA, McCain CM, McCune AR, McDade LA, McPeek MA, Near TJ, Price TD, Ricklefs RE, Roy K, Sax DF, Schluter D, Sobel JM, Turelli M (2007) Evolution and the latitudinal diversity gradient: speciation, extinction and biogeography. Ecol Lett 10(4):315–331. https://doi.org/10.1111/j.1461-0248.2007.01020.x
Moritz C, Potter S (2013) The importance of an evolutionary perspective in conservation policy planning. Mol Ecol 22(24):5969–5971. https://doi.org/10.1111/mec.12565
Münkemüller T, Lavergne S, Bzeznik B, Dray S, Jombart T, Schiffers K, Thuiller W (2012) How to measure and test phylogenetic signal. Methods Ecol Evol 3:743–756. https://doi.org/10.1111/j.2041-210X.2012.00196.x
Ngo NH, Nguyen QT, Phan QT, van Schingen M, Ziegler T (2019) A case study on trade in threatened Tiger Geckos (Goniurosaurus) in Vietnam including updated information on the abundance of the endangered G. catbaensis. Nat Conserv 33:1–19. https://doi.org/10.3897/natureconservation.32.33590
Ngo NH, Nguyen QH, Phan QT, Tran MH, Nguyen QT, Ziegler T, Rödder D (2021a) Vulnerability of an endemic Tiger Gecko (Goniurosaurus huuliensis) to climate change: modeling environmental refugia and implications for in-situ conservation. Salamandra 57(4):464–474
Ngo NH, Nguyen QH, Tran HM, Ngo HT, Le MD, Gewiss LR, van Schingen-Khan M, Nguyen TQ, Ziegler T (2021b) A morphological and molecular review of the genus Goniurosaurus, including an identification key. Eur J Taxon 751:38–67. https://doi.org/10.5852/ejt.2021.751.1379
Ngo NH, Nguyen QH, Phan QT, Nguyen QT, Rödder D, Gewiss RL, Ziegler T (2022a) Modeling the environmental refugia of the endangered Lichtenfelder’s Tiger Gecko (Goniurosaurus lichtenfelderi) towards implementation of transboundary conservation. Front Biogeogr 14(1):e51167. https://doi.org/10.21425/F5FBG51167
Ngo NH, Nguyen QH, Phan QT, Nguyen QT, van Schingen-Khan M, Ziegler T (2022b) Ecological niche overlap of two allopatric karst-adapted tiger geckos (Goniurosaurus) from northern Vietnam: microhabitat use and implications for conservation. J Nat Hist 56:37–40. https://doi.org/10.1080/00222933.2022.2120437
Ngo NH, Nguyen QH, Tran MH, Phan QT, Gewiss RL, Rödder D, Nguyen QT, Ziegler T (2022c) Living under the risk of extinction: population status and conservation needs assessment of a micro-endemic tiger gecko in Vietnam. Anim Biodivers Conserv 45(2):175–188. https://doi.org/10.32800/abc.2022.45.0175
Nguyen TQ (2011) Systematics, ecology, and conservation of the lizard fauna in northeastern Vietnam, with special focus on Pseudocalotes (Agamidae), Goniurosaurus (Eublepharidae), Sphenomorphus and Tropidophorus (Scincidae) from this country. PhD thesis, University of Bonn
Nguyen VS, Ho TC, Nguyen QT (2009) Herpetofauna of Vietnam. Edition Chimaira, Frankfurt, p 768
Nguyen LT, Schmidt HA, von Haeseler A, Minh BQ (2015) IQ-TREE: a fast and effective stochastic algorithm for estimating maximum likelihood phylogenies. Mol Biol Evol 32:268–274. https://doi.org/10.1093/molbev/msu300
Ohlemüller R, Anderson BJ, Araújo MB, Butchart SHM, Kudrna O, Ridgely RS, Thomas CD (2008) The coincidence of climatic and species rarity: high risk to small-range species from climate change. Biol Let 4:568–572. https://doi.org/10.1098/rsbl.2008.0097
Orlov NL, Ryabov SA, Nguyen TT, Nguyen TQ, Ho CT (2008) A new species of Goniurosaurus (Sauria: Gekkota: Eublepharidae) from north Vietnam. Russ J Herpetol 15(3):229–244. https://doi.org/10.30906/1026-2296-2008-15-3-229-244
Orr M, Smith TB (1998) Ecology and speciation. Trends Ecol Evol 13(2):502–506. https://doi.org/10.1016/S0169-5347(98)01511-0
Ota H (1998) Geographic patterns of endemism and speciation in amphibians and reptiles of the Ryukyu archipelago, Japan, with special reference to their paleogeographical implications. Res Popul Ecol 40:189–204. https://doi.org/10.1007/BF02763404
Palumbi S, Martin A, Romano S, McMillan WO, Stice L, Grabowski G (1991) The simple fool’s guide to PCR. Version 2.0. University of Hawaii, Honolulu, pp 1–24
Paradis E, Schliep K (2018) ape 5.0: an environment for modern phylogenetics and evolutionary analyses in R. Bioinformatics 35:526–528. https://doi.org/10.1093/bioinformatics/bty633
Pennell MW, Eastman JM, Slater GJ, Brown JW, Uyeda JC, FitzJohn RG, Alfaro ME, Harmon LJ (2014) geiger v2.0: an expanded suite of methods for fitting macroevolutionary models to phylogenetic trees. Bioinformatics 30(15):2216–2218. https://doi.org/10.1093/bioinformatics/btu181
Peterson AT (2011) Ecological niche conservatism: a time-structured review of evidence. J Biogeogr 38:817–827. https://doi.org/10.1111/j.1365-2699.2010.02456.x
Pyron AR, Costa GC, Patten MA, Burbrink FT (2014) Phylogenetic niche conservatism and the evolutionary basis of ecological speciation. Biol Rev 90(4):1248–1262. https://doi.org/10.1111/j.1469-8137.2012.04298.x
Qi S, Grismer LL, Lyu ZT, Zhang L, Li PP, Wang YY (2020) A definition of the Goniurosaurus yingdeensis group (Squamata, Eublepharidae) with the description of a new species. ZooKeys 986:127–155. https://doi.org/10.3897/zookeys.986.47989
Queiroz JS, Griswold D, Nguyen DT and Hall P (2013) Vietnam tropical forest and biodiversity assessment. US Foreign Assistance Act, Section 118/119 Report
Rambaut A, Drummond AJ (2014) TreeAnnotator v1. 7.0. https://doi.org/10.1186/1471-2148-7-214
Rambaut A, Suchard MA, Xie D, Drummond AJ (2014) Tracer v1.6. https://doi.org/10.1093/sysbio/syy032
Rato C, Harris DJ, Perera A, Carvalho SB, Carretero MA, Rödder D (2015) A combination of divergence and conservatism in the niche evolution of Tarentola mauritanica (Gekkota: Phyllodactylidae). PLoS ONE 10(5):e0127980. https://doi.org/10.1371/journal.pone.0127980
Ree RH, Smith SA (2008) Maximum likelihood inference of geographic range evolution by dispersal, local extinction, and cladogenesis. Syst Biol 57:4–14. https://doi.org/10.1080/10635150701883881
Revell LJ (2012) phytools: an R package for phylogenetic comparative biology (and other things). Methods Ecol Evol 3:217–223. https://doi.org/10.1111/j.2041-210X.2011.00169.x
Revell LJ (2013) Two new graphical methods for mapping trait evolution on phylogenies. Methods Ecol Evol 4:754–759. https://doi.org/10.1111/2041-210X.12066
Richardson DM, Whittaker RJ (2010) Conservation biogeography—foundations, concepts and challenges. Divers Distrib 16(3):313–320. https://doi.org/10.1111/j.1472-4642.2010.00660.x
Rödder D, Engler JO (2011) Quantitative metrics of overlaps in Grinnellian niches: advances and possible drawbacks. Glob Ecol Biogeogr 20:915–927. https://doi.org/10.1111/j.1466-8238.2011.00659.x
Rödder D, Lötters S, Öz M, Bogaerts S, Eleftherakos K, Veith M (2011) A novel method to calculate climatic niche similarity among species with restricted ranges—the case of terrestrial Lycian salamanders. Org Divers Evol 11:409–423. https://doi.org/10.1007/s13127-011-0058-y
Ronquist F (1997) Dispersal-vicariance analysis: a new approach to the quantification of historical biogeography. Syst Biol 46:195–203. https://doi.org/10.1093/sysbio/46.1.195
Ronquist F, Teslenko M, van der Mark P, Ayres DL, Darling A, Höhna B, Larget L, Liu L, Suchard MA, Huelsenbeck JP (2012) Mr. Bayes 3.2: efficient Bayesian phylogenetic inference and model choice across a large model space. Syst Biol 61:539–542. https://doi.org/10.1093/sysbio/sys029
RStudio Team (2018) RStudio: integrated development for R. RStudio, Inc., Boston
Salamin N, Wüest RO, Lavergne S, Thuiller W, Pearman PB (2010) Assessing rapid evolution in a changing environment. Trends Ecol Evol 25(12):692–698. https://doi.org/10.1016/j.tree.2010.09.009
Schluter D (2009) Evidence for ecological speciation and its alternative. Science 323(5915):737. https://doi.org/10.1126/science.1160006
Schoener TW (1970) Nonsynchronous spatial overlap of lizards in patchy habitats. Ecology 51:408–418. https://doi.org/10.2307/1935376
Seno T, Stein S, Gripp AE (1993) A model for the motion of the Philippine Sea plate consistent with NUVEL-1 and geological data. J Geophys Res 98:0148–0227. https://doi.org/10.1029/93jb00782
Sinervo B, Méndez-de-la-Cruz F, Miles DB, Heulin B, Bastiaans E, Villagrán-Santa Cruz M, Lara-Resendiz R, Martínez-Méndez N, Calderón-Espinosa ML, Meza-Lázaro RN, Gadsden H, Avila LJ, Morando M, De la Riva IJ, Sepulveda PV, Duarte Rocha CF, Ibargüengoytía N, Puntriano CA, Massot M, Lepetz V, Oksanen TA, Chapple DG, Bauer AM, Branch WR, Clobert J, Sites JW (2010) Erosion of lizard diversity by climate change and altered thermal niches. Science 328(5980):894–899. https://doi.org/10.1126/science.1184695
Smith SA, O’Meara BC (2012) treePL: divergence time estimation using penalized likelihood for large phylogenies. Bioinformatics 28:2689–2690. https://doi.org/10.1093/bioinformatics/bts492
Smith AB, Godsoe W, Rodríguez-Sánchez F, Wang HH, Warren D (2019) Niche estimation above and below the species level. Trends Ecol Evol 34(3):260–273. https://doi.org/10.1016/j.tree.201810.012
Soberón J (2007) Grinnellian and Eltonian niches and geographic distributions of species. Ecol Lett 10:1115–1123. https://doi.org/10.1111/j.1461-0248.2007.01107.x
Stein A, Gerstner K, Kreft H (2014) Environmental heterogeneity as a universal driver of species richness across taxa, biomes and spatial scales. Ecol Lett 17:866–880. https://doi.org/10.1111/ele.1227
Steinbauer MJ, Field R, Grytnes J, Trigas P, Ah-Peng C, Attorre F, Birks HJB, Borges PAV, Cardoso P, Chou C, De Sanctis M, de Sequeira MM, Duarte MC, Elias RB, Jump A (2016) Topography-driven isolation, speciation and a global increase of endemism with elevation. Glob Ecol Biogeogr 25(9):1097–1107. https://doi.org/10.1111/geb.12469
Sterling EJ, Hurley MM, Le DM (2006) Vietnam: a natural history. Yale University Press, New Haven. https://doi.org/10.1017/S0376892908004621
Suggitt AJ, Wilson RJ, Isaac NJB, Beale CM, Auffret AG, August T, Bennie JJ, Crick HQP, Duffield S, Fox R, Hopkins JJ, Macgregor NA, Morecroft MD, Walker KJ, Maclean IMD (2018) Extinction risk from climate change is reduced by microclimatic buffering. Nat Clim Change 8:713–717. https://doi.org/10.1038/s41558-018-0231-9
Teng LS, Lin AT (2004) Cenozoic tectonics of the China continental margin: insights from Taiwan. Geol Soc Lond Spl Publ 226:313–332. https://doi.org/10.1144/GSL.SP.2004.226.01.17
Thuiller W, Lavorel S, Araújo MB (2005) Niche properties and geographic extent as predictors of species sensitivity to climate change. Glob Ecol Biogeogr 14:347–357. https://doi.org/10.1111/j.1466-822X.2005.00162.x
Thuiller W, Georges D, Engler R, Breiner F (2016) biomod2: ensemble platform for species distribution modeling. R package version 3(3.1)
Trew BT, Maclean IMD (2021) Vulnerability of global biodiversity hotspots to climate change. Glob Ecol Biogeogr 30:768–783. https://doi.org/10.1111/geb.13272
Trifinopoulos J, Nguyen LT, von Haesele A, Minh BQ (2016) W-IQTREE: a fast online phylogenetic tool for maximum likelihood analysis. Nucleic Acids Res 44:W232–W235. https://doi.org/10.1093/nar/gkw256
Warren DL, Glor RE, Turelli M (2008) Environmental niche equivalency versus conservatism: quantitative approaches to niche evolution. Evolution 62(11):2868–2883. https://doi.org/10.1111/j.1558-5646.2008.00482.x
Wiens JJ, Graham CH (2005) Niche conservatism: integrating evolution, ecology, and conservation biology. Annu Rev Ecol Syst 36:519–539. https://doi.org/10.1146/annurev.ecolsys.36.102803.095431
Wiens JJ, Ackerly DD, Allen AP et al (2010) Niche conservatism as an emerging principle in ecology and conservation biology. Ecol Lett 13(10):1310–1324. https://doi.org/10.1111/j.1461-0248.2010.01515.x
Williams JW, Jackson ST, Kutzbach JE (2007) Projected distributions of novel and disappearing climates by 2100 AD. Proc Natl Acad Sci USA 104:5738–5742. https://doi.org/10.1073/pnas.0606292104
Yang JH, Chan BP (2015) Two new species of the genus Goniurosaurus (Squamata: Sauria: Eublepharidae) from Southern China. Zootaxa 3980:067–080. https://doi.org/10.11646/zootaxa.3980.1.4
Zhu XY, Chen GY, Román-Palacios C, Li Z, He ZQ (2020a) Goniurosaurus gezhi sp. nov., a new gecko species from Guangxi, China (Squamata: Eublepharidae). Zootaxa 4852:211–222. https://doi.org/10.11646/zootaxa.4852.2.6
Zhu XY, Shen CZ, Liu YF, Chen L, Li Z, He ZQ (2020b) A new species of Goniurosaurus from Hainan Island, China based on molecular and morphological data (Squamata: Sauria: Eublepharidae). Zootaxa 4772:349–360. https://doi.org/10.11646/zootaxa.4772.2.6
Zhu XY, Liu YJ, Bai Y, Roman-Palacios C, Li Z, He ZQ (2021) Goniurosaurus chengzheng sp. nov., a new species of Leopard Gecko from Guangxi, China (Squamata: Eublepharidae). Zootaxa 4996(3):555–568. https://doi.org/10.11646/zootaxa.4996.3.8
Zhu XY, Wu SY, Liu YJ, Bai Y, Román-Palacios C, Li Z, He ZQ (2022) Goniurosaurus wangshu sp. nov., a new species of Tiger Gecko from Guangdong, China (Squamata: Eublepharidae). Zootaxa 5188(6):544–558. https://doi.org/10.11646/zootaxa.5188.6.3
Acknowledgements
The authors thank the Vietnamese local authorities and forest protection departments in study sites. They are grateful to Theo Pagel and Christopher Landsberg (Cologne Zoo), Sinh V. Nguyen (IEBR, Hanoi), Lien V. Vu (VNMN, Hanoi), Tao T. Nguyen (IGR) for their support of conservation–based biodiversity research in Vietnam. Thanks to Huy Quoc Nguyen (VNMN), Tien Quang Phan, Hieu Minh Tran (IEBR), Thinh Van Nguyen (IGR), Laurenz Gewiss and Mona van Schingen-Khan (Federal Agency for Nature Conservation) who assisted during field surveys.
Funding
Open Access funding enabled and organized by Projekt DEAL. This research was supported by the Institute of Ecology and Biological Resources (Project code IEBR NV.01-23) and the Vietnam Academy of Science and Technology (VAST)—Japan Society for the Promotion of Science (JSPS) (Project code QTJP01.02/23-25). Field surveys were partially funded by Cologne Zoo, the Rufford Foundation (Project: 30597-1). Cologne Zoo is a partner of the World Association of Zoos and Aquariums (WAZA): Conservation Project 07011, 07012 (Herpetodiversity Research, Amphibian and Reptilian Breeding and Rescue Stations). The research of Hai Ngoc Ngo in Germany is funded by the German Academic Exchange Service (DAAD).
Author information
Authors and Affiliations
Contributions
HNN, DR and LG conceptualized the manuscript and computed the models, HNN and TQN provided field data, MDL and LG analyzed phylogenetic data, HNN and LG wrote the first draft. All authors read, revised and approved the final manuscript for publication.
Corresponding author
Ethics declarations
Conflict of interest
Authors declare no conflict of interest.
Informed consent
All the authors give the consent for publication of the article.
Additional information
Communicated by David Hawksworth.
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary Information
Below is the link to the electronic supplementary material.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.
About this article
Cite this article
Ngo, H.N., Rödder, D., Grismer, L. et al. Extraordinary diversity among allopatric species in the genus Goniurosaurus (Squamata: Eublepharidae): understanding niche evolution and the need of conservation measures. Biodivers Conserv 32, 1549–1571 (2023). https://doi.org/10.1007/s10531-023-02564-4
Received:
Revised:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10531-023-02564-4