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19 March 2018 A New Collared Lizard (Tropidurus: Tropiduridae) Endemic to the Western Bolivian Andes and Its Implications for Seasonally Dry Tropical Forests
André L.G. Carvalho, Luis Rolando Rivas, Ricardo Céspedes, Miguel T. Rodrigues
Author Affiliations +
Abstract

In this study we describe Tropidurus azurduyae, a new species of lizard endemic to the Andes. This species is restricted to inter-Andean dry valleys of central and southern Bolivia, within the ecoregion known as Bolivian Montane Dry Forests. It is currently known from the departments of Chuquisaca, Cochabamba, Potosí, and Santa Cruz, where it ranges in elevation from about 1000 to 2800 m. In addition, our analyses of closely related populations of Tropidurus from Argentina, Bolivia, Brazil, and Paraguay revealed undescribed species in central and northeastern Brazil and eastern Bolivia that render T. etheridgei Cei, 1982, paraphyletic. These results underscore the need for a comprehensive revision of peripheral and disjunct populations currently assigned to widely distributed species of Tropidurus. The phylogenetic relationships and distribution patterns of these new taxa concur with recent findings supporting seasonally dry tropical forests and open formations of dry vegetation from South America as distinct biotic units. Furthermore, they offer no support for seasonally dry tropical forests as closely related areas. In line with these discoveries, we refute biogeographic scenarios based exclusively on vicariance to explain the biogeographic history of Tropidurus.

INTRODUCTION

Bolivia is among the most neglected areas of the globe in terms of biodiversity research, and our knowledge of its lizard fauna is nothing but incomplete (Dirksen and De La Riva, 1999; Langstroth, 2005). In an attempt to remedy this situation, organizations such as Conservation International (CI) have funded rapid assessment programs (RAPs; Larsen, 2016), sending multidisciplinary teams to evaluate the state of biodiversity in some of Bolivia's most remote areas (Alonso et al., 2011). For instance, between 1991 and 1995, CI carried out a RAP6 in the lowlands and isolated mesa of the Noel Kempff Mercado National Park and surroundings (Killeen and Schulenberg, 1998). This inventory revealed the occurrence of 1094 vertebrates, 97 scarab beetles, and 2705 plants species within an area no larger than 750,000 hectares (7500 km2), and among those taxa, 29 were considered new. As part of that RAP, Harvey (1998) reported three new species of the lizard genus Tropidurus Wied, 1825, that were described shortly thereafter as Tropidurus callathelys, T. chromatops, and T. xanthochilus by Harvey and Gutberiet (1998). Nevertheless, even though that single genus (Tropidurus) was already known to occur in at least six of the nine Bolivian departments (Dirksen and De La Riva, 1999), ranging from isolated rock outcrops and savanna enclaves in the Amazon to seasonally dry tropical forests along the Andes, a comprehensive taxonomic assessment of highland populations remained undone.

In 2013, we visited the Torotoro National Park, Potosí Department, located in the heart of the Bolivian Montane Dry Forests (Olson et al., 2001; Crispieri et al., 2009). There, we found a new form of Tropidurus endemic to high-altitude formations of seasonally dry tropical forests known as “inter-Andean dry valleys” (López, 2003a, 2003b). This new species had been previously overlooked as T. etheridgei Cei, 1982, whose distribution range has been long assumed to comprise besides the inter-Andean dry valleys of central and southern Bolivia also the Chaco of northwestern Argentina, southeastern Bolivia, and western Paraguay, rock outcrops in eastern Bolivia and central Brazil, and disjunct patches of sandy habitats in central and northeastern Brazil (Cei, 1982; Rodrigues, 1987; Dirksen and De La Riva, 1999; Carvalho, 2013). In this paper, we describe this new form as the first species of the T. torquatus species group (per Frost et al., 2001) endemic to the Andes. Our morphological and molecular analyses of populations historically assigned to nominal T. etheridgei also revealed other undescribed species of Tropidurus in disjunct seasonally dry tropical forests and in open formations of dry vegetation in South America. The examination of the phylogenetic relationships and distribution of those taxa gave us the opportunity to critically examine the biogeographic history of these areas. In addition to the taxonomic description of our new Andean Tropidurus and notes on the systematic advances achieved based on the novel phylogeny produced, a summary of relevant biogeographic results is provided.

Material and Methods

Fieldwork and Study Area: Between 13–15 November 2013, two of us (A.L.G.C. and L.R.R.) visited the Torotoro National Park, Bolivia, for collection of specimens of the lizard genus Tropidurus. An illustration of the main habitats visited in Torotoro, prepuna and inter-Andean dry valleys, is shown in figure 1. The park, located in the homonymous municipality of Torotoro, Potosí Department, Charcas Province, ~85 km southeast of the municipality of Cochabamba (straight-line path), is the smallest protected area of Bolivia (Crispieri et al., 2009; fig. 2). Its area of 166 km2 encompasses semiarid landscapes from 1900 m to 3600 m in elevation, with numerous canyons and valleys, lying altogether within the domains of the Bolivian Montane Dry Forests (locally known as bosques secos montanos bolivianos or valles secos interandinos). This xeric ecoregion is restricted to central and southern Bolivia and comprises seasonal dry forests, wetland forests along rivers, and dry, sparsely vegetated slopes with contorted trees and shrubs, columnar cacti, and patches of bromeliads over bare or stony soils (Olson et al., 2001). The Bolivian Montane Dry Forests lie between the Andean Yungas and Chaco to the east, and the Puna to the west, at higher elevations, ranging from ∼1000 to 3300 m, but it is predominantly found between ∼1500 and 3000 m. Precipitation in this zone ranges from 200 to 650 mm (defining a marked, dry winter) and mean temperatures from 14°–19° C (López, 2003a).

Samples: Specimens were collected with the aid of rubber bands, euthanized with an overdose of 2% lidocaine, preserved with 10% unbuffered formalin, and then transferred to 70% ethyl alcohol solution. Before fixation, tissue samples (muscle) from the thigh of all individuals were collected and stored in absolute ethyl alcohol for subsequent molecular analyses. All specimens and tissue samples collected in Torotoro were deposited at the Museo de Historia Natural Alcide d'Orbigny (MHNC), Cochabamba, Bolivia. Collection permits were granted to us by the Bolivian Ministerio de Medio Ambiente y Agua (MMAyA permit #2298/2013). All specimens collected were assigned to the type series of the new species described herein; refer to Species Accounts for details on collections sites and catalog numbers.

Additional material employed in morphological comparisons and ethanol-preserved tissue samples (muscle, liver, finger, and tail tips) analyzed molecularly were obtained from the American Museum of Natural History, New York (AMNH and Ambrose Monell Cryo Collection—AMCC); Museo Nacional de Ciencias Naturales, Madrid (MNCN); Museo de Historia Natural Alcide d'Orbigny, Cochabamba, Bolivia (MHNC); Museo Nacional de Historia Natural del Paraguay, San Lorenzo, Paraguay (MNHNP); Museo de Historia Natural Noel Kempff Mercado, Santa Cruz de la Sierra, Bolivia (MNK); Miguel Trefaut Rodrigues Tissue Collection, Instituto de Biociências, Universidade de São Paulo, Brazil (MTR and nonstandardized acronyms); Museu de Zoologia da Universidade de São Paulo, Brazil (MZUSP); Universidade Federal do Mato Grosso, Cuiabá, Brazil (UFMT). Universidade Federal do Rio Grande do Sul, Porto Alegre, Brazil (UFRGS). In total, we analyzed 85 tissue samples, representing three out of the four Tropidurus species groups defined by Frost et al. (2001) (T. semitaeniatus group, T. spinulosus group, and T. torquatus group) plus outgroups. A list of the 109 specimens examined morphologically (and corresponding collection/field information) and a list of tissue samples, respective voucher specimens, and GenBank accession numbers is provided in appendices 14.

FIGURE 1.

Habitats visited in the Torotoro National Park, Potosí, Bolivia. A–D, Prepuna (18° 7′ 10.92″ S, 65° 48′ 30.24″ W — WGS84 system; ∼2798 m). E–G, Inter-Andean dry valleys at the type locality of Tropidurus azurduyae (18° 5′ 54.24″ S, 65° 44′ 57.48″ W — WGS84 system; ∼2264 m). H, Adult male of T. azurduyae, sighted (not collected) at the type locality of the species.

f01_01.jpg

Morphological Descriptions, Sex Determination, and Interspecific Variation: We adopted the terminology revised by Carvalho et al. (2016) for description of external morphological structures. Adult male specimens were identified based on the presence of colored patches of scales varying from yellow to black on the ventral side of thighs and precloacal flap. Males also have wider heads and thinner bodies than females of the same body size (Pinto et al., 2005; Ribeiro et al., 2012). Sex determination of juveniles is not as obvious, and required the examination of gonadal condition.

We collected morphometric data from the right side of 45 adult male and 49 adult female specimens of Tropidurus with the aid of a digital caliper (to the nearest 0.01 mm). We modified Carvalho et al.'s (2016) morphometric protocol by adding two variables: head length (HL), measured from the tip of the snout to the posterior end of the occipital region; and armpit to groin distance (AGD). In total, we analyzed 13 morphometric variables: SVL, snout-vent length; HH, head height; HL, head length; HW, head width; EOS, ear opening-snout distance; AL, arm length; FAL, forearm length; HDL, manus length; THL, thigh length; SL, shank length; FOL, foot length; AGD, armpit to groin distance; and TL, tail length. We calculated basic statistical descriptors (mean, standard deviation, and minimum and maximum values) for all variables and tested the assumptions of normality and variance homoscedasticity using Shapiro-Wilk and Bartlett test, respectively (Sokal and Rohlf, 1995). We log 10-transformed all morphometric variables and performed a principal component analysis (PCA; covariance matrix) to investigate morphometric variation. Linear discriminant analysis (LDA) was then used to test for morphometric differences among species (non-log-transformed data). We employed the leave-one-out cross-validation procedure to assess the accuracy of species reclassifications resulting from LDA. We did not incorporate variable TL into the multivariate analyses because a large portion of the specimens measured had broken, regrown, or missing tails. Size differences (SVL) among species were tested with analysis of variance (ANOVA) and post hoc Tukey-Kramer test.

We analyzed 51 male and 57 female specimens to investigate variation in scale counts among species. Meristic variables were tested for normality and variance homoscedasticity using Shapiro-Wilk and Bartlett test, respectively (Sokal and Rohlf, 1995). Following the same procedures adopted for morphometric data analyses, we employed PCA plus LDA to investigate meristic variation and test for differences in scale counts among species, avoiding multiple pairwise comparisons. All statistical analyses were carried out for each sex separately using R version 3.3.2 (R Core Team, 2017).

Phylogenetic Inference: All laboratory procedures employed for generation and manipulation of sequence data followed Carvalho et al. (2016). To infer the phylogenetic relationships of Tropidurus and determine the proper allocation of the new species under description within this genus, we analyzed four mitochondrial (12S, 16S, CO1, Cyt b) and six nuclear loci (BACH1, kif24, NTF3, PRLR, PTPN, SNCAIP). We initially sampled as ingroups one representative of each species previously sequenced and morphologically analyzed by Carvalho et al. (2016). In addition, because Andean populations assignable to the T. torquatus species group (per Frost et al., 2001) have been referred to in the literature as T. etheridgei (see Carvalho, 2013, for a review) and preliminary results by our team have indicated that that name might represent a species complex comprising, among others, our new Andean taxon, we broadened our molecular sampling to include individuals from multiple populations of T. etheridgei (sensu lato) throughout its distribution range in northern Argentina, central and southeastern Bolivia, central and northeastern Brazil, and western Paraguay. Because T. chromatops was recovered in our previous study (Carvalho et al., 2016) as sister of T. etheridgei (sensu stricto), we made the decision of including all samples of this species we had in hand in our analyses. We selected the tropidurines Microlophus quadrivittatus Tschudi, 1845, Plica plica (Linnaeus, 1758), T. semitaeniatus (Spix, 1825), T. spinulosus (Cope, 1862), and Uranoscodon superciliosus (Linnaeus, 1758), and the stenocercine Stenocercus quinarius Nogueira and Rodrigues (2006) as outgroups; the latter was chosen to root the phylogenetic trees produced.

TABLE 1.

Primers and PCR profiles for DNA amplification. Sequences encoding the mitochondrial genes 12S rDNA, 16S rDNA, COI, and Cyt b, and nuclear genes BACH1, kif24, NTF3, PRLR, PTPN, and SNCAIP, were employed for phylogenetic analyses.

t01a_01.gif

Continued

t01b_01.gif

Alignment, Model Selection, and Phylogenetic Analyses: To infer the relationships of Tropidurus our phylogenetic analyses followed the framework adopted by Carvalho et al. (2016, which see for details on data manipulation and analytical methods and table 1 for PCR protocols). In summary, alignments were performed in MAFFT version 7 (Katoh and Toh, 2008; Katoh and Standley, 2013) and concatenated in Sequence Matrix version 1.8 (Vaidya et al., 2011). We employed PartitionFinder version 2.1.1 (Lanfear et al., 2012, 2016) to determine the best-fit nucleotide substitution models and data partition schemes. All available models were compared, and the “greedy search” algorithm and linked branch lengths were selected for calculations of likelihood scores; Bayesian information criterion (BIC) was adopted for selecting among alternative partitioning strategies. For maximum-likelihood analyses (hereafter, ML), tree searches were performed in Garli version 2.1 (Zwickl, 2006). Starting tree topologies were generated using the stepwise-addition algorithm and the number of attachment points evaluated for each taxon to be added was set to 171. Our best-tree search was based on 100 replicates and the relative support of the clades recovered was assessed through 1000 nonparametric bootstrap replicates (Felsenstein 1985, 2004). We summarized bootstrap results using SumTrees (Sukumaran and Holder, 2010). All phylogenetic analyses were performed on a Mac OSX Yosemite 10.10.5, 3.4 GHz Intel core 17 processor, 16GB 1333 MHz DDR3. All alignments and trees produced in this study were made available for download from the AMNH Library Digital Repository ( https://doi.org/10.5531/sd.sp.29).

Genetic Distance: We calculated uncorrected genetic distances (p-distances) within and among species using MEGA version 7.0 (Kumar et al., 2016). Genetic distances were computed for partial fragments of Cyt b and 12S using the complete deletion method. Of the original 756 and 881 aligned sites of Cyt b and 12S, respectively, 330 bp and 878 bp were used for calculation of genetic distances after exclusion of sites containing missing data from sequence tips. We excluded samples [MTR] PNP 189–6207 and AMCC 204493 from genetic distance calculations of Cyt b and samples [MTR] 916015, [MTR] 916016, and [MTR] PNP187 from genetic distance calculations of 12S because the fragments sequenced for these samples were much shorter than the longest set of (aligned) overlapping fragments obtained for all other individuals. Cyt-b alignment contained no internal gap sites and 12S fragments contained 53 internal gap sites.

SPECIES ACCOUNTS

Tropiduridae Bell, 1843
Tropidurus Wied, 1825
Tropidurus azurduyae , n. sp.
Figures 1H, 3E–H, 4A–F

  • Holotype: MHNC-R 3011, adult male from Parque Nacional Torotoro, Potosí, Bolivia (18° 5′ 54.24″ S, 65° 44′ 57.48″ W — WGS84 system; ∼2264 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, G. Juchazara, E. Lujo, and F. Mamani in 13 November 2013.

  • Allotype: MHNC-R 3009, adult female, same locality as holotype (18° 5′ 53.88″ S, 65° 44′ 57.12″ W — WGS84 system; ∼2262 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, G. Juchazara, E. Lujo, and F. Mamani in 13 November 2013.

  • Paratypes: MHNC-R 3007, adult female, same locality as holotype (18° 6′ 15.48″ S, 65° 45′ 36.00″ W — WGS84 system; ∼2569), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, J. Choque, J. Kamaqui, and E. Lujo in 14 November 2013. MHNC-R 3008, adult female, same locality (18° 6′ 25.56″ S, 65° 45′ 27.36″ W — WGS84 system; ∼2579 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, J. Choque, J. Kamaqui, and E. Lujo in 14 November 2013. MHNC-R 3010, adult male, same locality (18° 5′ 52.32″ S, 65° 44′ 57.48″ W — WGS84 system; sim;2269 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, G. Juchazara, E. Lujo, and F. Mamani in 13 November 2013. MHNC-R 3012, adult male, same locality (18° 6′ 25.56″ S, 65° 45′ 25.92″ W — WGS84 system; ∼2566 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, J. Choque, J. Kamaqui, and E. Lujo in 14 November 2013. MHNC-R 3015, adult male, same locality (18° 6′ 25.92″ S, 65° 45′ 25.92″ W — WGS84 system; ∼2562 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, J. Choque, J. Kamaqui, and E. Lujo in 14 November 2013. MHNC-R 3016, adult male, same locality (18° 5′ 54.24″ S, 65° 44′ 55.32″ W — WGS84 system; ∼2556 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, G. Juchazara, E. Lujo, and F. Mamani in 13 November 2013. MHNC-R 3017, adult male, same locality (18° 5′ 55.32″ S, 65° 44′ 58.56″ W — WGS84 system; ∼2274 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, G. Juchazara, E. Lujo, and F. Mamani in 13 November 2013. MHNC-R 3020, adult male, same locality (18° 5′ 11.88″ S, 65° 45′ 44.28″ W — WGS84 system; ∼2596 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, J. Choque, J. Kamaqui, and E. Lujo in 14 November 2013. MHNC-R 3024, juvenile female, same locality (18° 5′ 55.32″ S, 65° 44′ 57.48″ W — WGS84 system; ∼2269 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, G. Juchazara, E. Lujo, and F. Mamani in 13 November 2013. MHNC-R 3026, juvenile female, same locality (18° 5′ 54.24″ S, 65° 44′ 55.32″ W — WGS84 system; ∼2256 m), collected by A.L.G. Carvalho, M.A. Sena, L.R. Rivas, G. Juchazara, E. Lujo, and F. Mamani in 13 November 2013.

  • Morphological Diagnosis: Tropidurus azurduyae is here morphologically diagnosed as a Tropidurus based on the observation of a set of characters suggested by Frost et al. (2001) as exclusive to the genus: skull not highly elevated at the level of the orbits; “flash” marks on underside of thighs present; circumorbitals distinct from other small supraorbital scales; lateral fringe not developed on both sides of fourth toes; enlarged middorsal scale row absent; tail terete; and hemipenis attenuate without apical disks. The presence of a maxilla not broad, nutritive foramina of maxilla strikingly enlarged, lingual process of dentary extending over lingual dentary process of coronoid, angular strongly reduced, and absence of medial centrale could not be examined without dissecting or clearing and staining specimens. These characters should be revised whenever larger series of individuals become available.

  • Tropidurus azurduyae is a member of the T. torquatus group per Frost et al. (2001). It differs from other species groups by lacking an enlarged middorsal scale row (well marked in species of the T. spinulosus group, especially in males), by exhibiting black “flash” marks on the underside of thighs and cloacal flap of adult males (yellow, cream, or orangey “flash” marks are present in males of the T. spinulosus group), and also by lacking a dorsoventrally flattened body (as observed in species of the T. semitaeniatus group and, more moderately, in T. bogerti).

  • Tropidurus azurduyae is the only species in the genus with lower flanks pigmented orange, a condition consistently observed in both sexes (fig. 3E–H). Its ventral head is darkly pigmented and offers contrast to the light circular blotches present on chin and also laterally (fig. 3G, H). The ground color of its throat is charcoal gray impregnated with strong orange coloration (fig. 3G, H). A pair of mite pockets is present on the lateral neck, with the posterior one larger; the anterior pocket originates lower than the posterior, but both usually end ventrally at the same level (fig. 3F). No pockets are found in the armpit and inguinal region of the new species. An elliptical or subrhomboidal black mark is present on the mid venter of adult males of T. azurduyae in addition to black “flash” marks on the underside of thighs and precloacal flap (fig. 3H). Tropidurus azurduyae is saxicolous, but may climb tree trunks and fallen logs occasionally (fig. 1H). In combination, this set of characters provides a safe diagnosis, distinguishing T. azurduyae from all other congeners.

  • Comparison with Other Species: Tropidurus azurduyae, T. cocorobensis, T. chromatops, T. etheridgei, T. hygomi, and T. psammonastes are the only species of the T. torquatus group that have two mite pockets on the lateral neck and lack differentiated skin folds or pockets in the axillary and inguinal regions. Although T. catalanensis, T. imbituba, and T. torquatus also have two mite pockets on the lateral neck, all three species exhibit 2-3 shallow granular areas in the axillary region and a fully developed granular inguinal pocket. The two pockets on the lateral neck of T. azurduyae are not exceptionally broadened nor deep, and they differ from the extremely enlarged lateral neck pockets of T. chromatops (fig. 5). They are also slightly distinct from the pockets of T. hygomi, which are oblique and deep, with the anterior one positioned more ventrally than the posterior one in both species. Tropidurus hygomi and T. azurduyae can be further distinguished by the presence of expanded scales covering the supraocular area of the former species. The anterior lateral neck pocket of T. azurduyae is coated with granular scales, while this same structure in T. psammonastes is coated with regular scales (only the posterior one is granular). For a more comprehensive summary of mite-pocket morphologies and their taxonomic distribution in the T. torquatus group, refer to Rodrigues (1987: figs. 1–13) and Carvalho et al. (2016: table 2, fig. 8).

  • Tropidurus azurduyae is saxicolous, and its ecology contrasts markedly with the psammophilous habit of three other species of the T. torquatus group with two lateral neck mite pockets, T. cocorobensis, T. hygomi, and T. psammonastes. It can also be distinguished from T. cocorobensis and T. hygomi based on its larger body size (SVL: 66.06–104.85 mm in males and 62.83–89.58 mm in females of T. azurduyae, 61.39–74.59 mm in males and 60.27–65.37 mm in females of T. cocorobensis, and 54.15–67.30 mm in males and 48.08–60.38 mm in females of T. hygomi). The new species also lacks the 2–4 well-marked black ocellar spots that decorate the upper flanks of T. cocorobensis anteriorly, from nuchal collar, just above the humerus, reaching to the middle of the body. Tropidurus azurduyae differs from T. chromatops in terms of coloration by lacking an intense burnt-red dorsal head and a facial mask with touches of blue and cream (figs. 5, 6A–D). The new species exhibits a champagne background, mottled with dark grayish-brown and lead pigmentation, and dark ventral head. This coloration is fairly distinct from the dirty-yellow dorsal background decorated with a brown reticulated pattern, and light ventral head ornate with a loose reticulum or semireticulum, found in T. etheridgei (pattern better marked in males than females; fig. 3A–D). Moreover, with regard to coloration, the lower flanks and guiar region pigmented in orange in both sexes is, to our knowledge, exclusive to T. azurduyae.

  • Description of Holotype (figs. 3F, H, 4A–F): Medium-sized specimen of Tropidurus, SVL 87.31 mm; head triangular, length 30% of SVL and width 71% of head length; skull not compressed, not strongly elevated at level of orbits; rostrum not noticeably shortened relative to most other species in the genus; scales of frontonasal region not imbricating posteriorly, lenticulate scale organs distributed on the head, more abundant on the frontonasal and supraocular areas; rostral tall, about 3× (in lateral view) as high as first supralabial, contacting first supralabials, first lorilabials, nasals, and two postrostrals; 1/1 postrostrals; nasal single, slightly protruding, pentagonal, elongated anteroposteriorly with the tip of the pentagon directed anteriorly, in contact with rostral; 6/7 enlarged supralabials followed by 3/6 smaller scales reaching the rictus oris, never contacting subocular; nostril elliptical, occupying about 1/3 of nasal, positioned posteriorly, directed posterolaterally; 3/3 canthals; anteriormost canthal separated from supralabials by 1/1 rows of lorilabials; 8/8 laminate superciliary scales weakly produced vertically; 1/1 dorsally keeled preoculars contacting third canthal and 3/3 loreals; 2/1 suboculars dors ally keeled, elongate, separated from supralabials by one row of lorilabials posteriorly; palpebrals granular; second row of palpebrals larger, with scale organ on tip, central palpebrals unpigmented, nearly translucent; pupil circular; 3/3 main rows of supraoculars, oblique internal row with 8/8, medial row with 8/8, external row with 7/7 scales, the enlarged internal ones occupying up to half the width of the supraocular area; 1/1 rows of small, angulate circumorbitals; 1/1 rows of short semilaminate scales separating circumorbitals from superciliaries; interparietal enlarged, about 1.2× longer than wide; parietal eye visible, positioned medially on the posterior limit of the first third of the interparietal scale; temporals slightly imbricate, keeled, at least 3× larger than lateral neck scales and smaller than dorsals and parietais; ear shaped like inverted keyhole, canal deep, largest diameter (∼5.5 mm) of ear opening 25% of ear opening to snout distance; tympanum translucent; preauricular fringe consisting of row of 6/6 smooth, lanceolate scales; width of mental 60% of the width of rostral; mental extending posteriorly to the level of half of the first adjacent infralabials; 7/7 enlarged infralabials followed by 3/3 smaller scales reaching the rictus oris; 4/4 angulate, enlarged postmentals; 1/1 postmentals in contact with first infralabial; first postmentals not in contact; 11/11 sublabials; 46 gulars, imbricating posteriorly.

  • Vertebral crest absent; 85 dorsals; 82 scale rows around midbody; 79 ventrals; dorsals large, strongly keeled and mucronate, particularly on the dorsal neck; keels on dorsal and caudal scales align forming continuous, longitudinal, slightly oblique lines observable macroscopically; postumeral region with small, nearly granular, smooth, nonmucronate scales, increasing in size, intensity of keels and mucronation toward the flanks; ventrals smooth, nonmucronate, imbricate, about half the size of dorsals; midventral, dark-pigmented “flash” mark present, not intensely marked, subrhomboidal; “flash” marks on underside of thighs formed by 6/6 rows of dark glandular scales; 13 cloacal scales, cloacal flap with 12 rows of dark precloacal glandular scales; supracarpal scales smooth near finger I and slightly keeled toward finger V, rhomboidal or subrhomboidal; supratarsal scales smooth toward finger I and keeled and mucronate toward finger V, rhomboidal; both supracarpals and supratarsals with very rare scale organ positioned on the distal end of the scale, when present; infracarpal and infratarsal scales carinate, tricarinate toward fingers and toes; fingers and toes thin, cylindrical, slightly compressed laterally; supradigital lamellae keeled, rhomboidal, scale organ positioned on the distal end of the scales, when present; infradigital lamellae tricarinate and mucronate, 17/17 under fourth finger + ungual, 26/24 under fourth toe + ungual, medial careen larger and more projected than laterals; claws long, curved; preaxial scales of forearm strongly keeled and mucronate grading to smooth scales with no or short mucrons and smaller size on ventral and postaxial surfaces; 28/28 tibial scales, keeled and mucronate; dorsal body scales large, keeled, mucronate; lateral neck scales several times smaller than dorsals; rictal, nuchal, postauricular, supraauricular, dorsolateral, and antegular fold absent; shallow postauricular depression present; oblique neck fold well marked defining two lateral neck mite pockets on each side of the neck; anteriormost mite pocket half the size and originating lower than the posteriormost, both ending ventrally at the same level; antehumeral fold present and well marked, coated with imbricate scales similar to those on lateral neck; gular fold incomplete medially; axillary and inguinal mite pockets absent; tail slightly compressed laterally, regrown, tapering from the end of the first third to a point; caudal verticils absent; scales of tail imbricate, keeled, mucronate, up to 3× larger than dorsals.

  • Coloration in Life (fig. 3F, H): Dorsal head with champagne background, mottled with brownish and lead pigmentation. A champagne facial stripe decorates the lateral head, covering labials, lorilabials, loreals, inferior portion of preocular and suboculars, lower temporals, and preauricular fringe. Keeled portion of preocular and suboculars, palpebrals, superciliaries, and upper temporals dark pigmented, similar in coloration to dorsal head. Iris golden brown. Mental region champagne grading into a lead ventral head with touches of champagne. Sublabial and posterolateral region of the head decorated with champagne blotches, 1–7 scales in size, that reach the area behind ear opening. Throat charcoal gray with intense orange pigmentation permeating its dark background until the antegular fold. Area between antegular fold and beginning of chest mottled with lead pigmentation and touches of yellow. Neck and dorsal body champagne, mottled with brownish and lead pigmentation; dark coloration more concentrated along the vertebral area. Nuchal collar black, well marked, nearly complete dorsally, formed by 4–5 rows of dark scales extending from humeral attachment to the vertebral area, outlined by 2–4 rows of champagne scales. Uppermost limits of flanks similar to dorsum, lower flanks pigmented in orange from axillary to inguinal region. Chest cream, anteriorly sprinkled with lead pigmentation. Ventral ground coloration cream; black spotted subrhomboidal mark oriented anteroposteriorly present on the mid venter. Limbs with champagne background and lead pigmentation forming a pattern similar to dorsum anteriorly (arms and thighs), and a slightly diffuse, stripelike ornamentation perpendicular to limb axis posteriorly, including forearms and legs and supracarpal and supratarsal regions, and digits. Femoral and precloacal “flash” marks well marked, black in color, 31/33 and 12 scales long, respectively. Tail greenish champagne, mottled with lead pigmentation anteriorly; regenerated section greenish champagne; ventral side of the whole tail pale cream.

  • Coloration in Preservative (fig. 4A–F): Overall coloration pattern of head and body preserved. Champagne background partially faded into pale cream and lead pigmentation became lighter, gaining a brownish tone. Facial stripe decorating the lateral head preserved. Same is true for the light blotches distributed over sublabial and posterolateral area of the head, and area behind ear opening. Originally lead-pigmented area of ventral head became brownish. Intense orange pigmentation of gular region faded almost completely, remaining a merely elusive orangey tone over brownish scales. Nuchal collar remained well marked. Orange coloration on the lower flanks was completely washed out, increasing the contrast between the now paler background and brownish mottled pigmentation that decorates the lateral body. Loss of orange pigmentation revealed irregular light blotches composing the mottled pattern on the flanks. Lead pigmentation sprinkled anteriorly on the chest became brownish. Venter preserved its cream aspect. Dark “flash” marks fully preserved underneath the thighs, cloacal flap, and mid venter. Limbs gained a slightly lighter background and brownish pigmentation in the place of original lead tones. Tail coloration nearly unaltered.

  • Measurements of Holotype (in mm): SVL 87.31, TL 96.08 (regrown), HH 13.02, EOS 22.11, HL 25.99, HW 18.58, AL 15.80, FAL 13.36, HDL 15.94, THL 21.16, SL 17.72, FOL 29.72, AGD 36.78.

  • Morphometrics: Tropidurus azurduyae is a middle-sized species of the T. torquatus group, with adult males ranging from 66.06 to 104.85 mm SVL and females from 62.83 to 89.58 mm SVL. This species is statistically indistinct in body size from its closest, formally described relatives, T. chromatops and T. etheridgei, but males of T. chromatops were found to be (marginally) larger than those of T. etheridgei (ANOVA SVL: males: df (degrees of freedom) = 2, sum of squares = 0.017, mean square = 0.008, F value = 3.563, p = 0.037; females: df = 2, sum of squares = 0.006, mean square = 0.003, F value = 1.668, p = 0.200; tables 23). In terms of shape, PCA captured extensive overlap among species and showed relatively similar contribution of most variables for morphometric groupings, while LDA showed better success discriminating groups (fig. 7; table 4). For males, LDA indicated FAL and EOS as important variables separating species in LD1, and EOS, FAL, and THL in LD2. For females, FAL and AL contributed more for species discrimination in LD1, and FOL, HW, and HL in LD2. LDA functions reached >85% correct reclassifications, distinguishing male individuals of all three species and female individuals of T. etheridgei and T. azurduyae (table 5). However, correct reclassifications dropped considerably with the implementation of the leave-one-out cross-validation procedure, indicating that morphometric parameters alone may not safely distinguish all species analyzed (table 5).

  • Meristics: Tropidurus chromatops, T. etheridgei, and T. azurduyae overlap at least partially in most scale counts (figs. 810; table 6). Tropidurus etheridgei has, in general, lower scale counts in comparison to the other species analyzed; exceptions were observed only in the number of subdigital lamellae (fig. 9). Number of gulars and scales around midbody differ between T. chromatops and T. etheridgei (males only), but cannot be used to fully distinguish any of these species from T. azurduyae (fig. 8; table 6). Although a few individuals overlap (fig. 9), T. azurduyae has in average a higher number of tibials than T. chromatops and T. etheridgei (table 6). PCA based on meristic variables showed complete separation between T. azurduyae and T. etheridgei, but not in relation to T. chromatops (fig. 10; table 7). Number of tibials provided the strongest contribution for species groupings in both PCA and LDA, followed by the number of gulars, ventrals, and subdigital lamellae (table 7). LDA effectively discriminated species, showing correct reclassification >90% in all cases but one (female T. chromatops). Even with the implementation of the leave-one-out cross-validation procedure, correct reclassifications remained high; T. chromatops was the only poorly discriminated species (table 7). In general, scale counts can be used to distinguish T. azurduyae from T. etheridgei, and this latter species from T. chromatops, but they may be insufficient to separate T. azurduyae from T. chromatops (though the number of tibials is informative in most cases). For specimens with overlapping scale counts, additional diagnostic characters treated in Comparisons with Other Species should be considered.

  • Etymology: The species name azurduyae is a noun in the feminine genitive case honoring Juana Azurduy de Padilla (Chuquisaca, Bolivia: July 12, 1780—May 25, 1862), one of the most distinguished Latin American leaders who bravely fought for the independence of the Spanish territory of Upper Peru, which comprised part of today's Bolivia and Peru, and formed along with Argentina, Uruguay, and Paraguay the Viceroyalty of the Río de La Plata during colonial times. Her memory remained nearly forgotten for more than a century, until President Cristina Kirchner conferred on her the title of General of the Argentinian Army in 2009, and in that same year, the Bolivian Senate promoted Juana Azurduy posthumously to the rank of Marshal of the Republic, declaring her “Liberator of Bolivia.” Although the biography of Juana Azurduy assuredly places her as one of the most important women of Latin America, the history of her fight for freedom and equality has not received enough attention outside history classes and political events. Naming Tropidurus azurduyae we do not aim to merely reverence her as a historical personage and revolutionary soldier, but to genuinely honor her intelligence, courage, and heroic actions against a male-dominated colonialist world whose roots remain alive at the present time. This is an affirmative action to remind all Latin American women and men of our female heritage of strength and combativeness.

  • For a more comprehensive biography of Juana Azurduy, refer to the work of the Argentinian writer Mario “Pacho” O'Donnnel (1994), available online ( http://www.portaldesalta.gov.ar/juana%20azurduy.htm). Those interested may follow the YouTube link ( https://youtu.be/SERg-8GKCNeA) to hear the song “Juana Azurduy” in the voice of the Argentinian singer Mercedes Sosa, honoring the valiant spirit of Juana Azurduy.

  • Distribution, Endemism, Natural History, and Conservation: Tropidurus azurduyae was discovered from its type locality, Torotoro National Park, Department of Potosí, Bolivia (figs. 12). There, it is abundant in the xerophytic inter-Andean valleys, not being found in adjacent habitats such as the prepuna, located at altitudes above ∼2800 m. Specimens deposited at the Museo de Historia Natural Noel Kempff Mercado (Santa Cruz) and Museo de Historia Natural Alcide d'Orbigny (Cochabamba) revealed the occurrence of T. azurduyae in several other localities to the north, south, and east of Torotoro. Currently, the species is known from the Bolivian departments of Chuquisaca, Cochabamba, Potosí, and Santa Cruz, ranging from approximately 1040 to 2764 m. (fig. 2).

  • Tropidurus azurduyae is endemic to the Bolivian Montane Dry Forests (Olson et al., 2001), restricted to inter-Andean dry valleys from central and southern Bolivia (López, 2003a, 2003b; fig. 2). This is the first species of the T. torquatus species group (per Frost et al., 2001) endemic to the Andes, and it reaches the highest altitudes among all Tropidurus. Tropidurus melanopleurus Boulenger, 1902, member of the T. spinulosus species group (per Frost et al., 2001), is the only other species in the genus recognized as an Andean endemic. However, it is found in more mesic habitats along the eastern Andean slopes, from river margins and foothills of 400–500 m to altitudes near 2000 m (Laurent, 1982; Schumacher and Barts, 2003). Tropidurus melanopleurus ranges from southeastern Peru to northwestern Argentina, crossing the Bolivian territory from north to south predominantly along the Yungas and the Tucuman-Bolivian forests (Meier, 1982; Cei, 1993; Dirksen and De La Riva, 1999; Rivadeneira, 2008; Carvalho, 2013). The species is known to be sympatric (but never syntopic) with T. azurduyae in just a few areas of inter-Andean dry valleys in the Department of Santa Cruz (e.g., La Angostura; E. Cortez, personal commun.). However, as in most of its distribution, it is restricted to quebradas (river margins), and thus it is absent in the harsh dry environments dominated by T. azurduyae.

  • The type locality and a few dry valley sites visited in Cochabamba are the only areas for which information on the natural history of T. azurduyae is available currently. The new species is heliophilous and basks over small to large rock blocks (40 cm to >150 cm in diameter), either isolated or forming large rock aggregations throughout the dry valleys. Tropidurus azurduyae occasionally uses the trunk of the contorted trees that dominate the landscape. The dry valleys of Torotoro have reddish, stony soil similar in color to the flanks and guiar region of the new species. Tropidurus azurduyae is territorial and reacts to invasion of its home range with aggressive head movements and body push-ups, but rapidly flees to holes underneath boulders, hides in crevices between rock blocks, or climbs up tree trunks if truly threatened. Our short visit to the type locality did not allow us to determine the exact period and pattern of activity of T. azurduyae; however, lizards were seen active even during the hottest periods of the day. Specimens were collected in Torotoro from the second half of the morning (around 11 am) to the second half of the afternoon (around 4 pm). In dry valleys sites from Cochabamba, T. azurduyae has been observed active throughout the whole year (including the winter), basking over rocks after approximately 8 am. Nothing is known about the diet of T. azurduyae, but a few lizards were observed feeding on ants at the type locality. Most specimens collected by us had their mite pockets filled with a large number of bright orange chigger-mite larvae (fig. 3F), likely trombiculids, but the specific identity of these ectoparasites has not been investigated.

  • The conservation status of the Bolivian Montane Dry Forests has been defined as critical (WWF, 2017), with habitat loss one of the most severe threats to this region (Ibisch and Mérida, 2003; Aguirre et al., 2009; Navarro, 2011) and other seasonally dry tropical forests around the globe (Janzen, 1988; Miles et al., 2006). Records of T. azurduyae (and other endemic taxa) obtained from museum specimens collected years or decades ago are, therefore, no guarantee that previously sampled populations persist to date. Although the local abundance of T. azurduyae in the protected Torotoro National Park and its broader distribution in the inter-Andean dry valleys from central and southern Bolivia indicate that the species is unlikely to be threatened, the lack of information about the size, connectivity, genetic parameters, and ecological requirements of local populations compels us to recommend its classification as “data deficient,” following the rules proposed by IUCN (2001).

  • FIGURE 2.

    Geographic distribution of Tropidurus azurduyae. Map shows the altimetric profile of Bolivia and its neighboring countries to illustrate the association of the new species with high-altitude habitats (inter-Andean dry valleys) that compose the Bolivian Montane Dry Forests ecoregion. Type locality (Torotoro National Park, Potosí, Bolivia; 18° 5′ 54.24″ S, 65° 44′ 57.48″ W — WGS84 system; ∼2264 m) is highlighted.

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    FIGURE 3.

    Live specimens of Tropidurus etheridgei Cei, 1982 and T. azurduyae. A, C, Adult male of T. etheridgei (AMNH-R 176273) from Orloff, Colonia 15, Filadelfia, Boquerón, Paraguay (22° 19′ 58.42″ S, 59° 55′ 00.02″ W — WGS84 system; ∼136 m). B, D, Adult female of T. etheridgei (AMNH-R 176277) from Estancia Esmeraldas, Boquerón, Paraguay (20° 59′ 15.81″ S 61° 59′ 27.90″ W — WGS84 system; ∼329 m). E, G, Adult female (allotype MHNC-R 3009) of T. azurduyae. F, H, Adult male (holotype MHNC-R 3011) of T. azurduyae.

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    FIGURE 4.

    Preserved holotype of Tropidurus azurduyae (adult male, MHNC-R 3011). A, Dorsal head. B, Ventral head. C, Lateral head. D, Ventral body. E, Lateral body. F, Dorsal body.

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    FIGURE 5.

    Adult male of Tropidurus chromatops Harvey and Gutberiet, 1998 (MHNC-R 3018), illustrating the expanded lateral neck mite pockets and the colorful facial mask with touches of blue and cream, characteristic of the species.

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    TABLE 2.

    Mean ± standard deviation and (in parentheses) minimum and maximum values of morphometric measurements (in mm) of the species analyzed. Abbreviations: SVL, snout-vent length; TL, tail length; HH, head height; HL, head lenght; HW, head width; EOS, ear opening-snout distance; AL, arm length; FAL, forearm length; HDL, manus length; THL, thigh length; SL, shank length; FOL, foot length; AGD, armpit to groin distance. Number of measured individuals is followed (between parentheses) by the number of individuals with fully grown tails. See Material and Methods for details on treatment of individuals with broken, regrown, or missing tails.

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    TABLE 3.

    Tukey-Kramer pairwise comparisons of mean snouth-vent length among Tropidurus species. Abbreviations: Tchr, T. chromatops; Teth, T. etheridgei; Tazu, T. azurduyae

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    TABLE 4.

    Summary of the principal component analyses and linear discriminant analyses performed on morphometric variables. PC, component loadings; LD, discriminant coefficients; EVL, eigenvalues; SD, standard deviations; % Variance, explained variances.

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    TABLE 5.

    Species reclassification rates based on the linear discriminant functions generated with morphometric and meristic data. Cross-validation results (leave-one-out method) shown within parentheses and correct classifications highlighted in boldface.

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    TABLE 6.

    Mean ± standard deviation and (in parentheses) minimum and maximum scale counts of the species analyzed.

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    TABLE 7.

    Summary of the principal component analyses and linear discriminant analyses performed on meristic variables. PC, component loadings; LD, discriminant coefficients; EVL, eigenvalues; SD, standard deviations; % Variance: explained variances.

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    FIGURE 6.

    Live specimens of Tropidurus chromatops Harvey and Gutberiet, 1998 from isolated granitic outcrops ∼30 km W Florida, Santa Cruz, Bolivia (14° 36′ 17.28″ S, 61° 29′ 32.64″ W — WGS84 system; ∼309 m). A, C, Adult female (MHNC-R 3003). B, D, Adult male (MHNC-R 3018).

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    MOLECULES

    Alignment and Partitioning: We compiled and aligned sequence data for 79 ingroup and six outgroup species, summing up 85 samples. For mitochondrial and nuclear genes, molecular coverage varied from 29 to 84 samples per fragment (34%–99%), with average coverage of 72 terminals (85%) regarding all 10 genes. Our molecular data set summed up to 7001 aligned sites, varying from 477–1211 per locus. A summary of taxon coverage, number of variable, conserved, parsimony informative sites, and singletons is shown in table 8. Details on selected nucleotide evolution models and partition schemes employed in ML analyses are shown in table 9.

    Phylogenetic Results (fig. 11): In agreement with previous results (Carvalho et al., 2016), our analysis recovered Tropidurus as paraphyletic, yet confirmed the monophyly of the T. torquatus species group. Uranoscodon superciliosus was recovered as sister of all other tropidurines and M. quadrivittatus as sister of a large clade formed by T. spinulosus, P. plica, T. semitaeniatus, and the T. torquatus species group. Nested within this large tropidurine clade, T. spinulosus was recovered as sister of P. plica, while T. semitaeniatus was placed as sister of the T. torquatus species group. Relationships among species in the T. torquatus group differed only slightly in relation to our previous phylogenetic hypothesis (Carvalho et al., 2016). Tropidurus hygomi was again supported as sister of all other species in this group. Tropidurus itambere and T. psammonastes were confirmed as closely related taxa and formed the sister group of all species but T. hygomi. Tropidurus sertanejo is now placed as sister of the remaining species, including the closely related Tropidurus species endemic to the Espinhaço Mountain Range, in Brazil, T. montantus (T. mucujensis + T. erythrocephalus). However, low-support values retrieved for nodes supporting several interspecific relationships around this section of the tree indicate topological instabilities resulting from conflicting phylogenetic signal recovered from mitochondrial and nuclear loci (see Carvalho et al., 2016, for details). Consequently, we expect future changes in the phylogenetic placement of T. sertanejo and related species. The same is true for the internal relationships in the clade comprising T. cororobensis ((T. imbituba + T. torquatus) (T. catalanensis + T. etheridgei complex)).

    FIGURE 7.

    Scatterplots of PC1 and PC2 generated by the principal component analyses and LD1 and LD2 generated by the linear discriminant analyses performed on morphometric variables. See table 4 for corresponding summary statistics. Figure color-coded following species labels in figure 11.

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    FIGURE 8.

    Boxplots showing variation in scale counts among Tropidurus chromatops, T. etheridgei, and T. azurduyae.

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    Our current analysis recovered Tropidurus etheridgei as paraphyletic and confirmed our suspicion that this name represents a species complex. This clade, referred to as the T. etheridgei species complex or simply T. etheridgei complex, is well supported and deeply nested within the T. torquatus species group, in turn, sister of T. catalanensis. Within the T. etheridgei species complex, an undescribed species sampled from disjunct patches of sandy habitats located in the domains of the Atlantic Dry Forests, in the states of Minas Gerais and Bahia, Brazil, was recovered as sister of all remaining species. Tropidurus azurduyae is sister of a clade formed by an undescribed species associated to limestone outcrops found in the Chiquitano Dry Forests/Pantanal/Cerrado contact, in the states of Mato Grosso and Mato Grosso do Sul (Brazil), and Department of Santa Cruz (Bolivia), plus the closely related T. chromatops, known from isolated granitic outcrops and from the Serranía de Huanchaca/Serra Ricardo Franco and surroundings, on the Bolivia-Brazil border, and T. etheridgei (sensu stricto), restricted (though widely distributed) to the Chaco of northern Argentina, western Paraguay, and southeastern Bolivia.

    FIGURE 9.

    Boxplots showing variation in scale counts among Tropidurus chromatops, T. etheridgei, and T. azurduyae.

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    Genetic Distances: Pairwise genetic distances estimated using Cyt-b fragments were, on average, approximately two times as high as those of 12S. However, a clear trend of increase in genetic differences correlated with phylogenetic distance was observed in both cases. The average pairwise genetic distances registered among species in the Tropidurus torquatus group were 11.04% (Cyt b) and 5.07% (12S), and ranged from 4.30% to 16.20% (Cyt b) and 1.60% to 7.60% (12S) (refer to table 10 for details). Average intraspecific genetic distances calculated for species composing the T. etheridgei species complex varied from 0% to 3.7% (Cyt b) and from 0% to 0.8% (12S), while average interspecific distances were up to five times higher, ranging from 6% to 9% (Cyt b) and 3% to 4% (12S). Similar values were observed between most species pairs within the T. torquatus group (see table 10). Although we agree that arbitrary genetic-distance cutoffs alone are by no means justifiable as criteria to define species limits (DeSalle et al., 2005; Padial et al., 2010), p-distance values can be informative to establish a molecular profile of populations and species. Indeed, p-distances calculated for Cyt-b and 12S fragments of Tropidurus corroborate the morphological and phylogenetic evidence we gathered. Overall, our results support a novel taxonomic framework that recognizes at least four distinct species under nominal T. etheridgei (see Taxonomic Advances).

    FIGURE 10.

    Scatterplots of PC1 and PC2 generated by the principal component analyses and LD1 and LD2 generated by the linear discriminant analyses performed on meristic variables (scale counts). See table 7 for corresponding summary statistics. Figure color-coded following species labels in figure 11.

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    TABLE 8.

    Taxon coverage, number of aligned, conserved, variable, parsimony-informative sites, and singletons present in the alignments of mitochondrial and nuclear loci.

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    Taxonomic Advances: Although morphological and morphometric conservatism and convergence in traits are known to be a common occurrence within tropidurine clades (Frost, 1992; Harvey and Gutberiet, 2000; Frost et al., 2001; Carvalho et al., 2016), a number of species with different levels of crypsis await description (Carvalho et al., 2016; Domingos et al., 2017). Adding up to recent findings (Carvalho, 2016; Carvalho et al., 2016), Tropidurus azurduyae represents one more example of a conspicuous but previously overlooked taxon. The description of this new species raises to 30 the number of valid names assigned to Tropidurus; however, revealing its existence and phylogenetic relationships is only the first step toward resolving T. etheridgei's paraphyly. The evidence gathered so far supports the recognition of T. etheridgei as a Chacoan endemic, restricted to western Paraguay, northern Argentina, and southeastern Bolivia (figs. 1112A). Hereafter, we recommend populations of T. etheridgei (sensu lato) found outside the Chaco, within the limits of the Atlantic Dry Forests, Chiquitano Dry Forests, Pantanal, and Cerrado, be referred as candidate species assignable to clades “Tropidurus n. sp. 1 Atlantic Dry Forests” and “Tropidurus n. sp. 2 Chiquitano/Pantanal/Cerrado” (figs. 1112A). These populations are being treated taxonomically elsewhere and formal names will be available soon.

    The discovery of Tropidurus azurduyae and two undescribed species underscores the need for a comprehensive revision of peripheral and disjunct populations assigned to Tropidurus species with wide distributions. Unfortunately, samples housed in herpetological collections are in great part restricted to specimens in alcohol, and lack tissue samples, photographs, and field notes describing morphological, ecological, and behavioral traits. For example, potentially useful traits for species discrimination, such as eye color, dorsal pattern, condition of mite pockets and skin folds, ecological habit, and substrate preferences are rarely described. Thus, we take the opportunity to make a call of attention to other taxonomists and professional collectors dealing with tropidurines to include fine details and photographs in their field notes, reports, and catalog records—information that preferably be incorporated into the database of the zoological collections chosen to house the specimens. This simple initiative is expected to facilitate the taxonomic revision of morphologically conservative clades in the future, including complexes of cryptic species within the T. torquatus group.

    TABLE 9.

    Data partitions and respective models of nucleotide evolution selected for maximum likelihood analysis.

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    BIOGEOGRAPHY

    The discovery of Tropidurus azurduyae and two other closely related undescribed species gives us the opportunity to critically review the historical association among dry areas in South America (Carvalho et al., 2013). This time, instead of investigating patterns of area relationships based on major biogeographic provinces (Morrone, 2004, 2006), we employed a scheme of areas that distinguishes seasonally dry tropical forests from savannas and dry spinose woodlands (following definitions in Werneck, 2011). The Atlantic Dry Forests, Bolivian Montane Dry Forests, and Chiquitano Dry Forests represented seasonally dry tropical forests in our analysis, and the Cerrado, Pantanal, and Chaco corresponded to additional open biogeographic units. Besides mapping species ranges and endemism, we summarized the biogeographic information contained in our taxon cladogram (fig. 11) by replacing species names with the names of their respective areas of occurrence. The area cladogram produced (fig. 12B) revealed two aspects of the biotic identity and historical relationships between seasonally dry tropical forests and open dry areas that carry important biogeographic implications. First, most areas analyzed7 were found to harbor an endemic species of the T. etheridgei species complex. Second, we did not find support for seasonally dry tropical forests as closely related biogeographic units.

    TABLE 10.

    Uncorrected p-distances among Cyt b (lower left) and 12S (upper right) fragments of all tropidurid species analyzed. Column 1:1. S. quinarius; 2. U. superciliosus; 3. M. quadrivittatus; 4. T. spinulosus; 5. P. plica; 6. T. semitaeniatus; 7. T. hygomi; 8. T. itambere; 9. T. psammonastes; 10. T. hispidus; 11. T. insulanus; 12. T. oreadicus; 13. T. sertanejo; 14. T. montanus; 15. T. mucujensis; 16. T. erythrocephalus; 17. T. cocorobensis; 18. T. imbituba; 19. T. torquatus; 20. T. catalanensis; 21. Tropidurus n. sp. 1; 22. Tropidurus n. sp. 2; 23. T azurduyae; 24. T. chromatops; 25. T. etheridgei.

    t10_01.gif

    FIGURE 11.

    Maximum likelihood tree based on four mitochondrial (12S, 16S, CO1, Cyt b) and six nuclear loci (BACH1, kif24, NTF3, PRLR, PTPN, SNCAIP). Nonparametric bootstrap values (1000 replicates) shown above or associated to branches. Dashed lines correspond to branches shortened for graphical purposes.

    f11_01.jpg

    Indeed, the distribution of endemism observed herein is consistent with studies that recognize the unique biotic identity of open dry areas (Silva, 1995; Nogueira et al., 2011; Gutiérrez and Marinho-Filho, 2017) versus seasonally dry tropical forests in South America (Prado and Gibbs, 1993; Silva et al., 2004; López et al., 2006; Queiroz, 2006; Werneck and Colli, 2006). Interestingly, endemics and codistributed taxa with disjunct distributions in seasonally dry tropical forests were for a long time assumed as evidence of the fragmentation of a formerly more extensive and contiguous biome that covered areas currently dominated by the Cerrado and the Amazon. More specifically, the “Pleistocene Arc hypothesis” states that seasonally dry tropical forests reached their maximum range during the Last Glacial Maximum (∼21,000 years bp), in the late Pleistocene, and formed an arc of dry vegetation that once crossed the heart of South America (Prado and Gibbs, 1993) and perhaps even Amazonian lowlands (Pennington et al., 2000). Nevertheless, contrary to empirical evidence gathered from raw distribution data and molecular evidence of plant and animal groups associated to seasonally dry tropical forests (Prado, 2000; Werneck and Colli, 2006; Gaetano et al., 2008), recent studies based on palaeodistribution modeling and reexamination of palynological records have failed to predict continuous dry forests in South America even during the Last Glacial Maximum (Mayle, 2004, 2006; Werneck et al., 2011; but see Collevatti et al., 2013). In consonance with these studies, we found no support for seasonally dry tropical forests as closely related areas (fig. 12B); therefore, we refute the strict vicariance scenario implied by the Pleistocene Arc hypothesis.

    In contrast, the inferred area-relationship patterns support area breakups resulting from vicariance as well as dispersals from core areas as relevant processes responsible for shaping the biogeographic history of Tropidurus. Our interpretation recognizes the close association between areas with markedly distinct ages and geological histories as evidence in favor of dispersal. For instance, the occurrence of endemic T. azurduyae in the dry valleys of central and southern Bolivia is hypothesized to reflect a dispersal event from open dry areas of central South America, followed by speciation in the xerophytic Andean slopes. The origin of high-altitude formations such as the dry valleys is contingent on the last phase of the Andean orogenesis, and consequently, the evolution of these areas is unlikely to be historically linked to ancient regions from central South America. López (2003b) pointed out that the Andes apparently reached half their present altitude only 10 Ma bp, and suggested that the intense speciation leading to the present flora found in the dry valleys of Bolivia likely took place in the Pliocene and extended even to the Pleistocene. In his phytogeographic analysis, Lopez (2003b) interprets the occurrence of very few genera and absence of endemic plant families in the inter-Andean dry valleys as evidence of a relatively recent origin of its flora. In the same manner, the evolution of the endemic fauna associated to the inter-Andean dry valleys must have taken place in a relatively recent period, regardless if it is derived from adjacent proto-Andean elements, lineages dispersed from central South America, or both.

    FIGURE 12.

    A, Geographic distribution of sampled populations of the Tropidurus etheridgei species complex. Symbols on the map are color coded as species labels on the ML tree shown in figure 11. B, Area cladogram summarizing area relationships patterns supported by the phylogeny of the Tropidurus etheridgei species complex.

    f12_01.jpg

    The position of the Atlantic Dry Forests in our area cladogram, indicating its early segregation in relation to all other seasonally dry tropical forests and open dry areas (fig. 12B), adds more complexity to the vicariance scenario proposed by Carvalho et al. (2013), where the uplift of the Brazilian Central Plateau in the Late Pliocene-Early Pleistocene (4-2 Ma) was hypothesized to have promoted geographic isolation and subsequent differentiation of distinct biotas in areas covered by the Caatinga, Cerrado, and Chaco. This earlier hypothesis disregarded the limits and independent history of the Atlantic Dry Forests and other seasonally dry tropical forests, and, consequently, failed to effectively address the biogeographic history of dry areas of South America. Interestingly, dynamic vegetation simulations and palaeodistribution models have supported long-term historical stability for disjunct seasonally dry tropical forest areas in South America during the Last Glacial Maximum, including the Chiquitano Dry Forests from eastern Bolivia (and the Caatinga, Missiones, and Piedmont nuclei of seasonally dry tropical forests; see Werneck, 2011, for a review). However, these models sustain the occurrence of the Chiquitano only from the Pleistocene (Werneck et al., 2011) or even the Holocene (Mayle, 2004), when it is predicted to have advanced southward from areas that are now covered by the Amazon in eastern Bolivia (Burbridge et al., 2004; Mayle, 2004; Mayle et al., 2007). A recent origin of the Chiquitano Dry Forests contrasts with the position occupied by this area in our area cladogram, where it appears closely related to the more ancient Cerrado and Chaco. We interpret this conflict as evidence that the broad distribution of Tropidurus n. sp. 2 Chiquitano/ Pantanal/Cerrado results from past dispersal and speciation in the Chiquitano, followed by recent distribution expansion toward adjacent areas. Thus, we predict recent range-expansion signatures in future phylogeographic analyses of this species.

    The close association between Cerrado and Chaco observed in our area cladogram (fig. 12B) is in disagreement with palaeodistribution models that recognize the Venezuelan Llanos as the biogeographical counterpart of the Cerrado in South America (Werneck et al., 2012). Further, floristic evidence associates the Chaco with more meridional biogeographic regions, including temperate dry formations such as the Monte (Pennington et al., 2004; Roig-Junent et al., 2006; Roig et al., 2009). Werneck (2011) appropriately noted that the Chaco fauna has been often described as widely distributed over other South American regions, and show only moderate diversity and endemism levels, possibly as a consequence of its central location and accessibility. Despite our current data sustain that the open corridor of dry vegetation formed by the Caatinga, Cerrado, and Chaco does not stand as a historical biogeographic unit, understanding the close association between Cerrado and Chaco will require further empirical studies. Future tests of historical links between their biotas, if any, will certainly benefit from comparative phylogenetic and phylogeographic frameworks involving multiple taxonomic groups.

    CONCLUDING REMARKS

    The taxonomic description and reconstruction of the phylogenetic relationships of Tropidurus azurduyae reflect on our efforts to advance the systematics of widely distributed complexes of cryptic species of Tropidurus. Because tropidurine fossils have not been discovered to date, we were unable to perform a safe chronological analysis to determine minimum ages for clades and species. However, the identification of endemic species restricted to the inter-Andean dry valleys from central and southern Bolivia and other seasonally dry tropical forests and open dry areas from South America allow us to expand the body of evidence supporting these areas as distinct biotic units. Furthermore, our results provide evidence against the Pleistocene Arc hypothesis, and call our attention to revisiting the biogeographic history of the dry areas of South America based on improved data sets and comparative analyses of a larger number of clades. For the first time, our results show with clarity that scenarios based exclusively on vicariance are unlikely to explain the complex biogeographic history of Tropidurus. Nevertheless, even if the distribution data and phylogenetic patterns recovered thus far allow us to rule out certain hypotheses in favor of others, determining the timeframe of the events involved in the diversification and biogeographic history of Tropidurus is crucial. Certainly, the incorporation of the time component (Donoghue and Moore, 2003) remains as a major challenge for us to fully understand the evolutionary history of this lizard clade (Carvalho et al., 2013).

    ACKNOWLEDGMENTS

    We express our sincerest gratitude to Eliana Lizarraga, Gabriel Callapa, Arturo Muñoz, and Teresa Camacho, from the Museo de Historia Natural Alcide d'Orbigny (MHNC), and to Kathia Rivero, Edson Cortez Cuellar, and Miguel Castro from the Museo de Historia Natural Noel Kempff Mercado (MNK) for the valuable advice and logistic support provided during fieldwork in Bolivia in 2013 and during analysis of specimens in both museums, in 2013 and 2017. We must also thank the Bolivian Ministerio de Medio Ambiente y Agua (MMAyA) and the Servicio Nacional de Sanidad Agropecuaria e Inocuidad Alimentaria (SENASAG) for collection permits and sanitary certification that allowed us to have access to specimens from Bolivia. We thank the administration of Torotoro National Park for support during our visit in 2013, and park rangers Eduardo Lujo, Felix Mamani, Geronimo Juchazara, Justino Kamaqui, and Juvenal Choque for guiding us inside the area of the park. We are also grateful to Marco Aurelio de Sena (Universidade de São Paulo) for his valuable help during the field trip to Torotoro.

    We are in debt to George Amato for making available the necessary facilities and resources for molecular lab work at the Sackler Institute for Comparative Genomics. We thank Ellen Trimarco, Mohammad Faiz, Stephen Gaughran, Ashley Yang, Melina Giakoumis, and Rebecca Hesch for all assistance provided during lab work at the Sackler Institute. This study counted on the valuable assistance from David Kizirian, Margaret Arnold, David Dickey, Rob Pascocello, and Lauren Vonnahme from the Department of Herpetology of the AMNH.

    We thank Carola Yovanovich (Universidade de São Paulo) for suggesting the specific epithet for the new species described herein. We also express our gratitude to Mariane Targino (Universidade de São Paulo) for carefully reviewing the original draft of the manuscript, and to referees Edgar Benavides (Yale University) and Julia Klaczko (Universidade de Brasília), for the insightful comments that helped to improve its final version. We thank Robert Voss and Mary Knight (AMNH Novitates) for the excellent scientific and production editorial support provided.

    The Explores Club, Andrew Sabin Family Foundation, the American Museum of Natural History (Richard Gilder Graduate School), and São Paulo Research Foundation (FAPESP) provided financial support for fieldwork and analysis of museum specimens in Bolivia. A.L.G.C. was supported by the Brazilian National Council for Scientific and Technological Development (CNPq grant no. 200798/2010-3) during his Ph.D. at the AMNH, and is currently supported by a postdoctoral fellowship from FAPESP (grant no. 2016/08249-6). Funding from CNPq and FAPESP allowed the completion of this work at the University of São Paulo. A.L.G.C. and M.T.R. thank FAPESP and CNPq for funding.

    REFERENCES

    1.

    Aguirre, L.F., et al. 2009. Libro rojo de la fauna silvestre de vertebrados de Bolivia. La Paz: Ministerio de Medio Ambiente y Agua, Bolivia. Google Scholar

    2.

    Alonso, L.E., J.L. Deichmann, S.A. McKenna, P. Naskrecki, and S.J. Richards. 2011. Still counting...: biodiversity exploration for conservation—the first 20 years of the Rapid Assessment Program. Arlington, VA: Conservation International. Google Scholar

    3.

    Benavides, E., R. Baum, D. McClellan, and J. Sites, Jr. 2007. Molecular phylogenetics of the lizard genus Microlophus (Squamata: Tropiduridae): aligning and retrieving indel signal from nuclear introns. Systematic Biology 56 (5): 776–797 Google Scholar

    4.

    Burbridge, R.E., F.E. Mayle, and T.J. Killeen. 2004. Fifty-thousand-year vegetation and climate history of Noel Kempff Mercado National Park, Bolivian Amazon. Quaternary Research 61 (2): 215–230. Google Scholar

    5.

    Caetano, S., et al. 2008. The history of seasonally dry tropical forests in eastern South America: inferences from the genetic structure of the tree Astronium urundeuva (Anacardiaceae). Molecular Ecology 17 (13): 3147–3159. Google Scholar

    6.

    Carvalho, A.L.G. 2013. On the distribution and conservation of the South American lizard genus Tropidurus Wied-Neuwied, 1825 (Squamata: Tropiduridae). Zootaxa 3640: 42–56. Google Scholar

    7.

    Carvalho, A.L.G. 2016. Three new species of the Tropidurus spinulosus group (Squamata: Tropiduridae) from eastern Paraguay. American Museum Novitates 3853: 1–44. Google Scholar

    8.

    Carvalho, A.L.G., M.R. Britto, and D.F. Silva. 2013. Biogeography of the lizard genus Tropidurus Wied-Neuwied, 1825 (Squamata: Tropiduridae): distribution, endemism, and area relationships in South America. PLoS ONE 8 (3): e59736. Google Scholar

    9.

    Carvalho, A.L.G., et al. 2016. A new Tropidurus (Tropiduridae) from the semiarid Brazilian Caatinga: evidence for conflicting signal between mitochondrial and nuclear loci affecting the phylogenetic reconstruction of South American collared lizards. American Museum Novitates 3852: 1–66. Google Scholar

    10.

    Cei, J.M. 1982. A new species of Tropidurus (Sauria, Iguanidae) from the arid chacoan and western regions of Argentina. Occasional Papers of the Museum of Natural History, University of Kansas 97: 1–10. Google Scholar

    11.

    Cei, J.M. 1993. Reptiles del noroeste, nordeste y este de la Argentina. Herpetofauna de las selvas subtropicales Puna y Pampas. Museo Regionale di Scienze Naturali Torino, Torino, Monografie 14: 1–949. Google Scholar

    12.

    Chernoff, B., and P.W. Willink. 1999. A biological assessment of aquatic ecosystems of the Upper Río Orthon Basin, Pando, Bolivia. RAP Bulletin of Biological Assessment 15. Washington: Conservation International. Google Scholar

    13.

    Collevatti, R.G., et al. 2013. Drawbacks to palaeodistribution modelling: the case of South American seasonally dry forests. Journal of Biogeography 40 (2): 345–358. Google Scholar

    14.

    Crispieri, G.A.G., F.E. Fontúrbel, and E. Richard 2009. Plan de manejo del Área Natural de Manejo Integrado Torotoro 2006–2016. La Paz: Ecodreams Multimedia/Fundación Emegece. Google Scholar

    15.

    DeSalle, R., M.G. Egan, and M. Siddall. 2005. The unholy trinity: taxonomy, species delimitation and DNA barcoding. Philosophical Transactions of the Royal Society B, Biological Sciences 360 (1462): 1905–1916. Google Scholar

    16.

    Dirksen, L., and I. De la Riva. 1999. The lizards and amphisbaenians of Bolivia (Reptilia, Squamata): Checklist, localities, and bibliography. Graellsia 55: 199–215. Google Scholar

    17.

    Domingos, F.M.C.B., G.R. Colli, A. Lemmon, E.M. Lemmon, and L.B. Beheregaray. 2017. In the shadows: phylogenomics and coalescent species delimitation unveil cryptic diversity in a Cerrado endemic lizard (Squamata: Tropidurus). Molecular Phylogenetics and Evolution 107: 455–465. Google Scholar

    18.

    Donoghue, M.J., and B.R. Moore. 2003 Toward an integrative historical biogeography. Integrative Comparative Biology 43 (2): 261–70. Google Scholar

    19.

    Felsenstein, J. 1985. Confidence-limits on phylogenies—an approach using bootstrap. Evolution 39 (4): 783–791. Google Scholar

    20.

    Felsenstein, J. 2004. Inferring phylogenies. Sunderland, MA: Sinauer Associates. Google Scholar

    21.

    Folmer, O., M. Black, W. Hoeh, R. Lutz, and R. Vrijenhoek. 1994. DNA primers for amplification of mitochondrial cytochrome c oxidase subunit I from diverse metazoan invertebrates. Molecular Marine Biology and Biotechnology 3 (5): 294–299. Google Scholar

    22.

    Frost, D.R. 1992. Phylogenetic analysis and taxonomy of the Tropidurus group of lizards (Iguania, Tropiduridae). American Museum Novitates 3033: 1–68. Google Scholar

    23.

    Frost, D.R., M.T. Rodrigues, T. Grant, and T.A. Titus. 2001. Phylogenetics of the lizard genus Tropidurus (Squamata: Tropiduridae: Tropidurinae): direct optimization, descriptive efficiency, and sensitivity analysis of congruence between molecular data and morphology. Molecular Phylogenetics and Evolution 21 (3): 352–371. Google Scholar

    24.

    Geurgas, S.R., and M.T. Rodrigues. 2010. The hidden diversity of Coleodactylus amazonicus (Sphaerodactylidae, Gekkota) revealed by molecular data. Molecular Phylogenetics and Evolution 54 (2): 583–593. Google Scholar

    25.

    Geurgas, S.R., M.T. Rodrigues, and C. Moritz. 2008. The genus Coleodactylus (Sphaerodactylinae, Gekkota) revisited: a molecular phylogenetic perspective. Molecular Phylogenetics and Evolution 49 (1): 92–101. Google Scholar

    26.

    Gutiérrez, E.E., and J. Marinho-Filho. 2017. The mammalian faunas endemic to the Cerrado and the Caatinga. ZooKeys 644: 105–157. Google Scholar

    27.

    Harvey, M.B. 1998. Reptiles and amphibians of Parque Nacional Noel Kempff Mercado. In T.J. Killeen and T.S. Schulenberg (editors), A biological assessment of Parque Nacional Noel Kempff Mercado, Bolivia. RAP Working Papers 10: 144–153. Washington, Conservation International. Google Scholar

    28.

    Harvey, M.B., and R.L. Gutberlet, Jr. 1998. Lizards of the genus Tropidurus (Iguania: Tropiduridae) from the Serranía de Huanchaca, Bolivia: new species, natural history, and a key to the genus. Herpetologica 54 (4): 493–520. Google Scholar

    29.

    Harvey, M.B., and R.L. Gutberiet, Jr. 2000. A phylogenetic analysis of the tropidurine lizards (Squamata: Tropiduridae), including new characters of squamation and epidermal microstructure. Zoological Journal of Linnean Society 128 (2): 189–233. Google Scholar

    30.

    Ibisch, P.L., and G. Mérida. 2003. Bio diversidad: la riqueza de Bolivia. Estado de conocimiento y conservación. Ministerio de Desarrollo Sostenible. Santa Cruz de la Sierra: FAN. Google Scholar

    31.

    IUCN [International Union for Conservation of Nature], 2001. IUCN Red List categories: version 3.1. Prepared by the IUCN Species Survival Commission. Internet resource ( http://www.iucnredlist.org/static/categories_criteria_3_1), accessed August 22, 2017. Google Scholar

    32.

    Janzen, D.H. 1988. Tropical dry forests: the most endangered major tropical ecosystem. In E.O. Wilson and F.M. Peter (editors), Biodiversity: 130–137. Washington: National Academy Press. Google Scholar

    33.

    Katoh, K., and D.M. Standley. 2013. MAFFT multiple sequence alignment software version 7: improvements in performance and usability. Molecular Biology and Evolution 30 (4): 772–780. Google Scholar

    34.

    Katoh, K., and H. Toh. 2008. Recent developments in the MAFFT multiple sequence alignment program. Briefings in Bioinformatics 9 (4): 286–298. Google Scholar

    35.

    Killeen, T.J., and T.S. Schulenberg, 1998. A biological assessment of Parque Nacional Noel Kempff Mercado, Bolivia. RAP Working Papers 10. Washington: Conservation International. Google Scholar

    36.

    Kumar, S., G. Stecher, and K. Tamura. 2016. MEGA7: molecular evolutionary genetics analysis version 7.0 for bigger datasets. Molecular Biology and Evolution 33 (7): 1870–1874. Google Scholar

    37.

    Lanfear, R., B. Calcott, S.Y.W. Ho, and S. Guindon. 2012. PartitionFinder: combined selection of partitioning schemes and substitution models for phylogenetic analyses. Molecular Biology and Evolution 29 (6): 1695–1701. Google Scholar

    38.

    Lanfear, R., P.B. Frandsen, A.M. Wright, T. Senfeid, and B. Calcott. 2016. PartitionFinder 2: new methods for selecting partitioned models of evolution for molecular and morphological phylogenetic analyses. Molecular Biology and Evolution 34 (3): 772–773. Google Scholar

    39.

    Langstroth, R.P. 2005. Adiciones probables y confirmadas para la saurofauna boliviana. Kempffiana 1 (1): 101–128. Google Scholar

    40.

    Larsen, T.H. 2016. Core standardized methods for rapid biological field assessment. Arlington: Conservation International. Google Scholar

    41.

    Laurent, R.F. 1982. Variacion y dimorfismo sexual en el complejo Tropidurus melanopleurus-pictus (Iguanidae). In P.J. Salinas (editor), Actas del VIII Congreso Latinoamericano de Zoología 1: 621–626. Google Scholar

    42.

    López, R.P. 2003a. Diversidad florística y endemismo de los valles secos bolivianos. Ecología en Bolivia 38 (1): 27–60. Google Scholar

    43.

    López, R.P. 2003b. Phytogeographical relations of the Andean dry valleys of Bolivia. Journal of Biogeography 30 (11): 1659–1668. Google Scholar

    44.

    López, R.P., D.L. Alcázar, and M.J. Macía. 2006. The arid and dry plant formations of South America and their floristic connections: new data, new interpretation. Darwiniana 44 (1): 18–31. Google Scholar

    45.

    Mayle, F.E. 2004. Assessment of the Neotropical dry forest refugia hypothesis in the light of palaeoecological data and vegetation model simulations. Journal of Quaternary Science 19 (7): 713–720. Google Scholar

    46.

    Mayle, F.E. 2006. The late Quaternary biogeographical history of South American seasonally dry tropical forests: Insights from palaeo-ecological data. In R.T. Pennington, G.P. Lewis, and J.A. Ratter (editors), Neotropical savannas and seasonally dry forests: plant diversity, biogeography and conservation: 395–416. Boca Raton: CRC Press. Google Scholar

    47.

    Mayle, F.E., R.P. Langstroth, R.A. Fisher, and P. Meir. 2007. Long-term forest-savannah dynamics in the Bolivian Amazon: implications for conservation. Philosophical Transactions of the Royal Society B, Biological Sciences 362 (1478): 291–307. Google Scholar

    48.

    Meier, H. 1982. Zwei seltene Tropidurus—Arten aus Bolivien. Herpetofauna 4 (19): 10–12. Google Scholar

    49.

    Miles, L., et al. 2006. A global overview of the conservation status of tropical dry forests. Journal of Biogeography 33 (3): 491–505. Google Scholar

    50.

    Montambault, J.R. 2002. Informes de las evaluaciones biológicas de Pampas del Heath, Perú, Alto Madidi, Bolivia, y Pando, Bolivia. RAP Bulletin of Biological Assessment 24. Washington: Conservation International. Google Scholar

    51.

    Morrone, J.J. 2004. Panbiogeografia, componentes bióticos y zonas de transición. Revista Brasileira de Entomologia 48 (2): 149–162. Google Scholar

    52.

    Morrone, J.J. 2006. Biogeographic areas and transition zones of Latin America and the Caribbean Islands based on panbiogeographic and cladistic analyses of the entomofauna. Annual Review of Entomology 51: 467–494. Google Scholar

    53.

    Navarro, G. 2011. Clasificación de la vegetación en Bolivia. Santa Cruz de la Sierra: Centro de Ecología Difusión Simón I. Patiño. Google Scholar

    54.

    Nogueira, C., S. Ribeiro, G.C. Costa, and G.R. Colli. 2011. Vicariance and endemism in a Neotropical savanna hotspot: distribution patterns of Cerrado squamate reptiles. Journal of Biogeography 38 (10): 1907–1922. Google Scholar

    55.

    O'Donnnel, M.P. 1994. Juana Azurduy, la teniente coronela. Buenos Aires: Planeta. Google Scholar

    56.

    Olson, D.M., et al. 2001. Terrestrial ecoregions of the world: a new map of life on Earth: a new global map of terrestrial ecoregions provides an innovative tool for conserving biodiversity. BioScience 51 (11): 933–938. Google Scholar

    57.

    Padial, J.M., A. Miralles, I. De la Riva, and M. Vences. 2010. The integrative future of taxonomy. Frontiers in Zoology 7: 16. Google Scholar

    58.

    Palumbi, S.R. 1996. Nucleic acids II: the polymerase chain reaction. In D.M. Hillis, C. Moritz, and B.K. Mable (editors), Molecular systematics, 2nd ed.: 205–247. Sunderland, MA: Sinauer Associates. Google Scholar

    59.

    Parker, T.A., III , and B. Bailey. 1991. A biological assessment of the Alto Madidi region and adjacent areas of northwest Bolivia May 18–June 15, 1990. RAP Working Papers 1. Washington: Conservation International. Google Scholar

    60.

    Parker, T.A., III , R.B. Foster, L.H. Emmons, and B. Bailey. 1993. The lowland dry forests of Santa Cruz, Bolivia: a global conservation priority. RAP Working Papers 4. Washington: Conservation International. Google Scholar

    61.

    Pennington, R.T., D.E. Prado, and C.A. Pendry. 2000. Neotropical seasonally dry forests and Quaternary vegetation changes. Journal of Biogeography 27 (2): 261–273. Google Scholar

    62.

    Pennington, R.T., et al. 2004. Historical climate change and speciation: Neotropical seasonally dry forest plants show patterns of both Tertiary and Quaternary diversification. Philosophical Transactions of the Royal Society B, Biological Sciences 359 (1443): 515–538. Google Scholar

    63.

    Pinto, A.C.S., H.C. Wiederhecker, and G.R. Colli. 2005. Sexual dimorphism in the Neotropical lizard, Tropidurus torquatus (Squamata, Tropiduridae). Amphibia-Reptilia 26 (2): 127–137. Google Scholar

    64.

    Portik, D.M., P.L. Wood, Jr. , J.L. Grismer, E.L. Stanley, and T.R. Jackman. 2012. Identification of 104 rapidly-evolving nuclear protein-coding markers for amplification across scaled reptiles using genomic resources. Conservation Genetics Resources 4 (1): 1–10. Google Scholar

    65.

    Prado, D.E. 2000. Seasonally dry forests of tropical South America: from forgotten ecosystems to a new phytogeographic unit. Edinburgh Journal of Botany 57 (3): 437–461. Google Scholar

    66.

    Prado, D.E., and P.E. Gibbs. 1993. Patterns of species distributions in the dry seasonal forests of South America. Annals of the Missouri Botanical Garden 80 (4): 902–927. Google Scholar

    67.

    Queiroz, L.P. 2006. The Brazilian Caatinga: phytogeographical patterns inferred from distribution data of the Leguminosae. In R.T. Pennington, G.P. Lewis, and J.A. Ratter (editors), Neotropical savannas and seasonally dry forests: plant diversity, biogeography and conservation: 121–157. Boca Raton: CRC Press. Google Scholar

    68.

    R Core Team. 2017. R: a language and environment for statistical computing. R Foundation for Statistical Computing, Vienna. Internet resource ( http://www.R-project.org), accessed July 22, 2017. Google Scholar

    69.

    Ribeiro, L.B., N.B Silva, and E.M.X. Freire. 2012. Reproductive and fat body cycles of Tropidurus hispidus and Tropidurus semitaeniatus (Squamata, Tropiduridae) in a caatinga area of northeastern Brazil. Revista Chilena de Historia Natural 85 (3): 307–320. Google Scholar

    70.

    Rivadeneira, E.Y.D. 2008. Variación geográfica del complejo Tropidurus melanopleurus (Sauria: Tropiduridae). Undergraduate thesis, Facultad de Ciencias Puras y Naturales, Carrera Biología, Universidad Mayor de San Andrés, La Paz, Bolivia. Google Scholar

    71.

    Rodrigues, M.T. 1987. Sistemática, ecologia e zoogeografia dos Tropidurus do grupo torquatus ao sul do Rio Amazonas (Sauria, Iguanidae). Arquivos de Zoologia 31 (3): 105–230. Google Scholar

    72.

    Roig, F.A., S. Roig-Junent, and V. Corbalán. 2009. Biogeography of the Monte Desert. Journal of Arid Environments 73 (2): 164–172. Google Scholar

    73.

    Roig-Junent, S., M.C. Domínguez, G. Flores, and C. Mattoni. 2006. Biogeographic history of South American arid lands: A view from its arthropods using TASS analysis. Journal of Arid Environments 66 (3): 404–420. Google Scholar

    74.

    Schulenberg, T.S., and K. Awbrey. 1997. A rapid assessment of the humid forests of South Central Chuquisaca, Bolivia. RAP Working Papers 8. Washington: Conservation International. Google Scholar

    75.

    Schumacher, R., and M. Barts. 2003. Tropidurus melanopleurus Boulenger. Sauria (Suppl.) 25 (3): 591—596. Google Scholar

    76.

    Silva, J.M.C. 1995. Biogeographic analysis of the South American Cerrado avifauna. Steenstrupia 21: 49–67. Google Scholar

    77.

    Silva, J.M.C., M. Tabarelli, M.T. Fonseca, and L.V. Lins. 2004. Biodiversidade da Caatinga: áreas e ações prioritárias para a conservação. Brasília: Ministério do Meio Ambiente/Universidade Federal de Pernambuco. Google Scholar

    78.

    Sokal, R.R., and F.J. Rohlf. 1995. Biometry: the principles and practice of statistics in biological research, 3rd ed. New York: W.H. Freeman and Co. Google Scholar

    79.

    Sukumaran, J., and M.T. Holder. 2010. DendroPy: a Python library for phylogenetic computing. Bioinformatics 26 (12): 1569–1571. Google Scholar

    80.

    Vaidya, G., D.J. Lohman, and R. Meier. 2011. SequenceMatrix: concatenation software for the fast assembly of multi-gene datasets with character set and codon information. Cladistics 27 (2): 171–180. Google Scholar

    81.

    Werneck, F.P. 2011. The diversification of eastern South American open vegetation biomes: historical biogeography and perspectives. Quaternary Science Reviews 30 (13–14): 1630–1648. Google Scholar

    82.

    Werneck, F.P., and G.R. Colli. 2006. The lizard assemblage from seasonally dry tropical forest enclaves in the Cerrado biome, Brazil, and its association with the Pleistocenic Arc. Journal of Biogeography 33 (11): 1983–1992. Google Scholar

    83.

    Werneck, F.P., G.C. Costa, G.R. Colli, D.E. Prado, and J.W. Sites, Jr. 2011. Revisiting the historical distribution of seasonally dry tropical forests: New insights based on palaeodistribution modelling and palynological evidence. Global Ecology and Biogeography 20 (2): 272–288. Google Scholar

    84.

    Werneck, F.P., C. Nogueira, G.R. Colli, J.W. Sites, Jr. , and G.C. Costa. 2012. Climatic stability in the Brazilian Cerrado: implications for biogeographical connections of South American savannas, species richness and conservation in a biodiversity hotspot. Journal of Biogeography 39 (9): 1695–1706. Google Scholar

    85.

    Whiting, A.S., A.M. Bauer, and J.W. Sites, Jr. 2003. Phylogenetic relationships and limb loss in sub-Saharan African scincine lizards (Squamata: Scincidae). Molecular Phylogenetics and Evolution 29 (3): 582–598. Google Scholar

    86.

    WWF. 2017. South America: in the mountain valleys of southern central Bolivia. Internet resource ( https://www.worldwildlife.org/ecoregions/nt0206), accessed August 20, 2017. Google Scholar

    87.

    Zwickl, D.J. 2006. Genetic algorithm approaches for the phylogenetic analysis of large biological sequence datasets under the maximum likelihood criterion. Ph.D. dissertation, University of Texas at Austin. Google Scholar

    Notes

    [1] 6 In addition to the RAP carried out in the Noel Kempff Mercado National Park and surroundings (Killeen and Schulenberg, 1998), CI supported five other RAPs in Bolivia between 1990 and 1997, sampling aquatic environments of the Río Orthon Basin in Pando (Chernoff and Willink, 1999) and terrestrial sites of the Alto Madidi region (Parker and Bailey, 1991), Lowland Dry Forests of Santa Cruz (Parker et al., 1993), South Central Chuquisaca (Schulenberg and Awbrey, 1997), and Pando and Alto Madidi (Montambault, 2002). During these studies, species of the lizard genus Tropidurus were only registered in localities visited in the departments of Santa Cruz (see main text) and Chuquisaca (T. melanopleurus).

    [2] 7 The Chiquitano Dry Forests and Pantanal are exceptions, sharing an undescribed species of the Tropidurus etheridgei complex (figs. 1112A). It is likely, however, that the distribution of “Tropidurus n. sp. 2 Chiquitano/Pantanal/Cerrado,” and also “Tropidurus n. sp. 1 Atlantic Dry Forests,” actually follows the occurrence of dry forests associated to limestone formations found in central and northeastern South America (e.g., some geomorphological formations of the “Bambui group”). The ecological and biogeographic associations of both species must be revisited after analysis of additional populations and field observations.

    Appendices

    APPENDIX 1

    List of Samples Analyzed Morphologically and Molecularly

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    APPENDIX 2

    Gazetteer of Samples Analyzed

    Italicized names are those of the largest political units (states, departments, or provinces) within each country. Geographic coordinates marked with asterisks (*) were obtained directly in the field by the authors (or research team members). Other geographic coordinates were either obtained from collection's labels or georeferenced online using Google Earth Pro, version 7.3.1.4507.

    ARGENTINA

    • 1. Chaco, Fuerte Esperanza (25.1607° S, 61.8390° W)

    • 2. Córdoba, road between La Higuera and Estancia Jesuitica La Candelaria, 1.8 km E Piedra Blanca, Cruz del Eje (31.0442° S, 64.9983° W)

    • 3. Formosa, Ruta Nacional 81, Puesto Policia de Formosa, Salta-Formosa limit, 3 km E Capitan Page, Matacos (23.6939° S, 62.3383° W)

    • 4. La Rioja, Aimogasta, 2 km entrance of “Finca Ascha,” Arauco (28.5855° S, 66.9446° W)

    • 5. Salta, Bermejo River margin, 10 km W El Carmen, Oran (23.3318° S, 63.9870° W)

    • 6. Salta, Los Colorados, Anta (24.5833° S, 63.1833° W)

    • 7. Salta, Ruta Provincial 41, 8.6 km S split Ruta Provincial 52, 92 km NE Joaquin V., Anta (24.6341° S, 63.4518° W)

    • 8. Santiago del Estero, Route between Villa Ojo de Agua and Lomitas Blancas, Sierra de Ambargasta, 34.8 km W Villa Ojo de Agua, 14.8 km W Amiman, Ojo de Agua (29.3582° S, 63.9498° W)

    BOLIVIA

    • 9. Chuquisaca, El valle carretera Sucre-Cochabamba (before Mojtulo), Oropeza (18.8253° S, 65.1122° W)

    • 10. Chuquisaca, Machareti, Tati, Machareti, Luis Calvo (20.8025° S, 63.3763° W)

    • 11. Cochabamba, 1/2 Km from Río Julpe, Pojo, Carrasco (17.5893° S, 64.8549° W)

    • 12. Cochabamba, Aiquile (18.2020° S, 65.1667° W)

    • 13. Cochabamba, Buena Vista, Pasorapa (18.5500° S, 64.5610° W)

    • 14. Cochabamba, Capinota (17.7167° S, 66.2500° W)

    • 15. Cochabamba, Caramarca, Quillacollo (17.4318° S, 66.3105° W)

    • 16. Cochabamba, Cerro Cota, Quillacollo (17.4208° S, 66.3126° W)

    • 17. Cochabamba, Huañacota, Capinota (17.5568° S, 66.1716° W)

    • 18. Cochabamba, Playa Ancha, Capinota (17.6693° S, 66.2445° W)

    • 19. Cochabamba, Vinto Chico, Quillacollo (17.4327° S, 66.3186° W)

    • 20. Potosí, Toro Toro, Charcas (18.1016° S, 65.7672° W)

    • 21. Potosí, Torotoro National Park (18.1072° S, 65.7572° W)*

    • 22. Potosí, Torotoro National Park (18.1071° S, 65.7576° W)*

    • 23. Potosí, Torotoro National Park (18.1071° S, 65.7572° W)*

    • 24. Potosí, Torotoro National Park (18.1043° S, 65.7600° W)*

    • 25. Potosí, Torotoro National Park (18.1033° S, 65.7626° W)*

    • 26. Potosí, Torotoro National Park (18.0987° S, 65.7493° W)*

    • 27. Potosí, Torotoro National Park (18.0987° S, 65.7496° W)*

    • 28. Potosí, Torotoro National Park (18.0984° S, 65.7493° W)*

    • 29. Potosí, Torotoro National Park (18.0984° S, 65.7487° W)*

    • 30. Potosí, Torotoro National Park (18.0983° S, 65.7492° W)*

    • 31. Santa Cruz, Campamento Las Torrez, San Ignacio de Velasco, Velasco (13.6551° S, 60.8123° W)

    • 32. Santa Cruz, Cueva de Anamal, Vallegrande (18.0896° S, 64.1125° W)

    • 33. Santa Cruz, El Tholar, Moro Moro, Vallegrande (18.4201° S, 64.2928° W)

    • 34. Santa Cruz, Estancia Valparaiso, Mairana, Florida (18.0445° S, 63.9455° W)

    • 35. Santa Cruz, Itembeguazú, Cordillera (19.3500° S, 63.3833° W)

    • 36. Santa Cruz, Margin of Matara River, Pampagrande, Florida (18.0989° S, 64.1696° W)

    • 37. Santa Cruz, Mataral 5 km E, Pampagrande, Florida (18.0932° S, 64.1730° W)

    • 38. Santa Cruz, Mataral, Pampagrande, Florida (18.1153° S, 64.2157° W)

    • 39. Santa Cruz, Pampa Negra, Moro Moro, Vallegrande (18.5253° S, 64.2937° W)

    • 40. Santa Cruz, Pampagrande, Florida (18.0896° S, 64.1125° W)

    • 41. Santa Cruz, Pampagrande, Florida (18.0868° S, 64.1125° W)

    • 42. Santa Cruz, Pozo del Monte, Cordillera (20.2850° S, 63.2541° W)

    • 43. Santa Cruz, Puesto Militar 27 de Noviembre, Char agua, Cordillera (20.0131° S, 61.9042° W)

    • 44. Santa Cruz, Rock outcrops 30 km W Florida (14.6064° S, 61.4924° W)*

    • 45. Santa Cruz, Rock outcrops 30 km W Florida (14.6054° S, 61.4922° W)*

    • 46. Santa Cruz, Rock outcrops 30 km W Florida (14.6048° S, 61.4924° W)*

    • 47. Santa Cruz, Saipina, San Rafael, Manuel Maria Caballero (18.1077° S, 64.5641° W)

    • 48. Santa Cruz, Santiago de Chiquitos, Cerro del Arco, Roboré, Chiquitos (18.3460° S, 59.5532° W)

    • 49. Santa Cruz, Tatarenda, Camiri, Cordillera (19.1064° S, 63.5141° W)

    • 50. Santa Cruz, Torrecillas, Moro Moro, Vallegrande (18.4903° S, 64.3230° W)

    • 51. Santa Cruz, Vallegrande, Chañara, Vallegrande (18.5679° S, 64.1216° W)

    • 52. Santa Cruz, Villa Merced, Pampagrande, Florida (18.0937° S, 64.1883° W)

    • 53. Santa Cruz, Yapiroa, Charagua, Cordillera (19.6056° S, 62.5750° W)

    • 54. Tarija, La Central, Villamontes, Gran Chaco (21.2273° S, 63.5744° W)

    • 55. Tarija, Serranía Aguar ague, 17 km from Villa Montes toward Entre Ríos (21.3039° S, 63.5646° W)

    BRAZIL

    • 56. Amazonas, Lago Chaviana, Itapuru, right margin of Purus River, Beruri (4.3104° S, 61.8160° W)*

    • 57. Bahia, Caetité (14.0633° S, 42.5121° W)*

    • 58. Bahia, Correntina (13.4259° S, 44.7337° W)*

    • 59. Bahia, Correntina (13.4253° S, 44.7334° W)*

    • 60. Bahia, Estação Ecológica Serra Geral do Tocantins, Formoso do Rio Preto (10.6800° S, 46.1508° W)*

    • 61. Bahia, Fazenda Santo Antônio, Condeúba (14.9336° S, 41.9496° W)*

    • 62. Bahia, Ibiraba, Barra (10.8000° S, 42.8333° W)*

    • 63. Bahia, Lagoa do Abaeté, Salvador (12.9442° S, 38.3578° W)*

    • 64. Bahia, Morro do Chapéu (11.4893° S, 41.3344° W)*

    • 65. Bahia, Mucugê (13.0117° S, 41.3889° W)

    • 66. Bahia, Nova Rodelas (8.9833° S, 38.8000° W)*

    • 67. Bahia, RPPN Pé da Serra, Ibotirama (12.1450° S, 43.0523° W)*

    • 68. Mato Grosso, Cáceres (16.5165° S, 57.8369° W)

    • 69. Mato Grosso, Guarantã do Norte (9.6831° S, 54.9628° W)*

    • 70. Mato Grosso, Tangará da Serra (14.4346° S, 58.3104° W)

    • 71. Mato Grosso do Sul, Corumbá (18.7310° S, 56.7233° W)

    • 72. Minas Gerais, Arinos (15.9107° S, 46.1132° W)*

    • 73. Minas Gerais, Diamantina (18.2373° S, 43.6036° W)

    • 74. Minas Gerais, Parque Nacional Cavernas do Peruaçu, Januária (15.1551° S, 44.3094° W)*

    • 75. Minas Gerais, Parque Nacional Cavernas do Peruaçu, Januária (15.1547° S, 44.3051° W)*

    • 76. Minas Gerais, Parque Nacional Cavernas do Peruaçu, Januária (15.1544° S, 44.3030° W)*

    • 77. Minas Gerais, Primeira cachoeira do Rio Urucuia, Buritis (15.5953° S, 46.2494° W)*

    • 78. Rio de Janeiro, Restinga de Grussaí, São João da Barra (21.6812° S, 41.0305° W)*

    • 79. Rio Grande do Sul, Manoel Viana (29.5859° S, 55.4840° W)

    • 80. Santa Catarina, Imbituba (28.2389° S, 48.6528° W)

    • 81. São Paulo, Piedade (23.7196° S, 47.4153° W)

    • 82. Sergipe, Santo Amaro das Brotas (10.7858° S, 36.9781° W)

    CHILE

    • 83. Antofagasta, Punta Blanca (24.5211° S, 69.7114° W)*

    GUYANA

    • 84. Potaro-Siparuni, Magdalen's Creek Camp, near (± 300 yds) NW bank of the Konawaruk River [∼25 mi (linear) WSW Mabura Hill] (5.2186 ° N, 59.0453° W)

    PARAGUAY

    • 85. Boquerón, Destacamento Militar Número 1, III Cuerpo de Ejército, 5a Division de Infanteria, Mayor Pablo Lagerenza (20.3766° S, 60.5340° W)*

    • 86. Boquerón, Destacamento Militar Número 1, III Cuerpo de Ejército, 5a Division de Infantería, Mayor Pablo Lagerenza (20.3755° S, 60.5335° W)*

    • 87. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9877° S, 61.9911° W)*

    • 88. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9855° S, 61.9867° W)*

    • 89. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9853° S, 61.9870° W)*

    • 90. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9851° S, 61.9865° W)*

    • 91. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9846° S, 61.9861° W)*

    • 92. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9798° S, 61.9763° W)*

    • 93. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9797° S, 61.9762° W)*

    • 94. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9788° S, 61.9737° W)*

    • 95. Boquerón, Estancia Esmeraldas, General Eugenio A. Garay (20.9787° S, 61.9754° W)*

    • 96. Boquerón, Orloff, Colonia 15, Mariscal José Félix Estigarribia (22.3332° S, 59.9242° W)*

    • 97. Boquerón, Orloff, Colonia 15, Mariscal José Félix Estigarribia (22.3331° S, 59.9160° W)*

    • 98. Boquerón, Orloff, Colonia 15, Mariscal José Félix Estigarribia (22.3329° S, 59.9167° W)*

    • 99. Boquerón, Orloff, Colonia 15, Mariscal José Félix Estigarribia (22.3176° S, 59.9081° W)*

    • 100. Boquerón, Parque Nacional Teniente Agripino Enciso (21.1891° S, 61.6707° W)*

    • 101. Boquerón, Rodeo Trebol, Loma Plata (22.3439° S, 59.8619° W)*

    APPENDIX 3

    GenBank Accession Numbers of Mitochondrial Sequences

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    tA03b_01.gif

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    APPENDIX 4

    GenBank Accession Numbers of Nuclear Sequences

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    © American Museum of Natural History 2018
    André L.G. Carvalho, Luis Rolando Rivas, Ricardo Céspedes, and Miguel T. Rodrigues "A New Collared Lizard (Tropidurus: Tropiduridae) Endemic to the Western Bolivian Andes and Its Implications for Seasonally Dry Tropical Forests," American Museum Novitates 2018(3896), 1-56, (19 March 2018). https://doi.org/10.1206/3896.1
    Published: 19 March 2018
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