Research Article |
Corresponding author: Jakob von Tschirnhaus ( jakob.vontschirnhaus@gmail.com ) Corresponding author: Claudio Correa ( ccorreaq@udec.cl ) Academic editor: Uri García-Vázquez
© 2021 Jakob von Tschirnhaus, Claudio Correa.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
von Tschirnhaus J, Correa C (2021) The definitive rediscovery of Telmatobius halli (Anura, Telmatobiidae) at its historic type locality and its synonymy with T. dankoi and T. vilamensis. ZooKeys 1079: 1-33. https://doi.org/10.3897/zookeys.1079.69036
|
Telmatobius halli was the first representative of its genus to be described exclusively for Chile, yet for 85 years no new individuals could be located due to the vagueness with which its type locality was described. The type series was collected by one of the members of the International High Altitude Expedition to Chile (IHAEC) of 1935. Recently, three studies successively claimed to have located the type locality in different places. The third study proved, according to the chronicles of the IHAEC, that the actual locality is Miño, at the origin of the Loa River, where currently there are no published records of Telmatobius. In this study, additional documentary antecedents and graphic material are provided that corroborate that Miño is indeed the type locality of T. halli. Additionally, the recently rediscovered Telmatobius population from Miño and the environment it inhabits are described. The external characteristics of the frogs are consistent with the description of T. halli. Furthermore, molecular phylogenetic analyses were performed that showed that T. halli, T. dankoi, and T. vilamensis, all known only from their type localities in Chile, comprise a clade without internal resolution. A detailed comparison of the diagnoses of the three species revealed that the few phenotypic differences between these taxa were based on characteristics that vary widely within and between populations of the genus, hence their conspecificity is proposed. The implications of this synonymy for the taxonomy, biogeography, and conservation of the Telmatobius from the extreme south of its distribution in Chile are discussed.
Amphibia, Chile, Loa River, lost frog, phylogeny, Puna, taxonomy
The genus Telmatobius Wiegmann, 1834 is one of the few anuran taxa that has managed to diversify in the high Andes (
In Chile, nine species of Telmatobius, seven of them endemic, are currently recognized (
As in the case of other Chilean amphibian genera (Alsodes Bell, 1843; Eupsophus Fitzinger, 1843) (
Among the endemic species of Chile, Telmatobius halli Noble, 1938 stands out for its complex taxonomic history. Dr Frank Gregory Hall collected the type series (adults and larvae) in the context of the International High Altitude Expedition to Chile (IHAEC), an endeavor that took place in 1935 and whose principal purpose was to study the effects of low-oxygen environments of high elevation on the human physiology and the body’s acclimatization response (
Geographic context of this study A distribution of all Telmatobius populations known from the southern range of the genus in Chile (20°55'–22°55'S). Light grey area = Chilean territory, dark grey area = Bolivian territory, grey lines = limits of the sub-basins, star = study site, diamonds = type localities B topographic relief of the surroundings of Miño. Grey lines = limits of the sub-basins. Montt is the name provided by the IHAEC for the Collahuasi Copper Mine C satellite image of Miño. 1) Concrete pool, 2) ruins of mining settlement, 3) sampling point, a) Miño River, b) Nacimiento Creek, c) Loa River.
Recently,
Altogether, 83 years after its description and despite the multiple recent hypotheses about the location of its type locality and identity, T. halli is still a lost frog and no specimens have ever been seen since the collection of the type series (
The diary of Ross McFarland, one of the members of the IHAEC, was requested from the Ross A. McFarland Collection in Aerospace Medicine and Human Factors Engineering at the Wright State University Archives. The diary is listed as “Box 63, Folder 5: Ross McFarland’s Diary (May 1935–September 1935)” in the collection’s inventory (
On 31 October 2020, a field trip to the site called Miño (21°12'S, 68°40'W; 3900 m elevation; Calama Commune, El Loa Province, Antofagasta Region, Chile) was performed to locate the frog population that was described as T. halli (
As biosecurity measures to prevent the spreading of chytridiomycosis and other infectious diseases, we disinfected car tires, boots, and utensils with F10 Super Concentrate Disinfectant (Health and Hygiene Pty.) at a concentration of 1:250 (
We made a general description of the study area, considering the topography of the landscape and more specific conditions at microhabitat level. We measured the stream dimensions at various points and took air and water temperatures at different times of the day. The composition of the adjacent vegetation along the stream was ascertained and a nocturnal survey was undertaken to detect possible sympatric amphibians.
Both, adults and larvae, identified as Telmatobius, were collected during the daytime from the stream using a hand net. The sampling site was ~ 300 m upstream from the pool identified as the historical place where T. halli was collected (see details in Results). The animals were measured, photographed, and finally released back to the capture site. Each individual was handled separately with an unused pair of disposable nitrile gloves (
In order to obtain bioacoustic data, an AudioMoth recording unit (
During the night, the AudioMoth took a measurement of the air temperature every 15 minutes, but the sensor only has an accuracy of ± 3 °C (
Seven morphometric features were measured on 11 adult specimens (
Three tadpoles (Gosner stages 36–37) were anesthetized by immersing them in a buffered solution of MS-222 (0.2%) (
The DNA was extracted with a commercial kit (Promega ReliaPrepTM gDNA Tissue Miniprep System, Madison, WI) following the manufacturer’s instructions. We obtained fragments of two mitochondrial genes, 16S rRNA and cytochrome b (cytb), the same fragments that were used in the phylogenetic analyses of
The sequences of both fragments were aligned with MUSCLE (
We collected all available information on the morphology of T. halli and the two populations to which the same name was assigned before being formally described as different species (T. dankoi and T. vilamensis) to compare their diagnostic characters as well as the proposed differences between them. The morphological details were obtained from the literature as follows: T. halli (
As pointed out in
Historic and current panoramic view of the area surrounding the concrete swimming pool in Miño A panorama extracted from video footage from the IHAEC, 1935. Yellow arrows indicate rock formations that are easily recognizable B current state of the habitat. Red rectangle = location of the concrete pool. The mountain in the left background is Miño Volcano.
Regarding McFarland’s video material (Suppl. material
As expected, the remains of the mentioned concrete swimming pool were found at 21°12'01"S, 68°40'09"W (3,900 m) (Fig.
The Loa River originates mainly from meltwater from throughout its upper drainage basin, where snow accumulates during austral winter. Several temporal ravines also gather the characteristic precipitations during the austral summer months (December to March), known as Altiplanic winter (
For the first few kilometers, the riverbed is a broad and dry wadi named Miño River. Only ~ 4 km north of Miño, the arid riverbed gradually turns greener and ends in a small bog with grass tussocks, covering an area of ~ 5 ha. No significant water flow was registered during this time of the year (late October). At Miño, there are some well-preserved ruins of an old mining camp from the 18th and 19th centuries at both sides of the bog (
From this point on, the river bears the name Loa, as it receives its first permanent tributary, the “Estero Nacimiento” creek (
Below the confluence, the river suddenly turns into a pronounced canyon with vertical cliffs. The concrete pool is located precisely at the beginning of the canyon. Soon after, the river gets a little broader, forming larger natural ponds and sections with rapids. The canyon goes on in a similar manner for almost 100 km, until reaching the Conchi water reservoir.
Currently known Telmatobius populations from the southern range of the genus in Chile (20°55'–22°55'S). Localities are ordered from north to south (Fig.
Species | Locality | Elevation | References |
---|---|---|---|
T. chusmisensis | Copaquire | 3,540* |
|
T. fronteriensis | Puquios | 4,150 |
|
T. chusmisensis | Quebrada Chiclla | 4,550* |
|
T. chusmisensis | Quebrada Choja | 3,500* |
|
T. philippii | Quebrada del Inca | 3,800 | Cuevas and Formas (2002) |
T. philippii | Quebrada de Amincha | 3,800 | Cuevas and Formas (2002) |
T. halli | Miño | 3,900* | this study |
Telmatobius cf. philippii | Aguas Calientes1 | 3,717 |
|
Telmatobius cf. philippii | Ascotán Salt Flat (springs 2, 3, 5, 6, 7 and 11) | ~ 3,720 |
|
T. halli (previously T. dankoi) | Ojo de Opache (introduced there in 2019) | 1,960* |
|
T. halli (previously T. dankoi) | Las Cascadas | 2,260 |
|
T. halli (previously T. vilamensis) | Vilama River | 2,250* |
|
At the sampling point, the current of the Nacimiento Creek flows rapidly, though the terrain is not very steep. The stream is between 2.5 and 5 m broad and 25–50 cm deep. The water is clear and the bottom is mostly sandy with some stones and scarce detritus at the bends. The margins are almost entirely covered with vegetation, mainly Festuca chrysophylla Phil. and a few bushes of Parastrephia lucida (Meyen) Cabrera. The overhanging grass cushions are ideal refugia for the frogs, forming at times gallery-like cavities along the riverbank. At some points inside the stream, patches of Myriophyllum aquaticum (Vell.) Verdc. can be found, alternating with mats of undetermined filamentous green algae.
At the pool site, the bottom is also sandy; however, there is a little more mud and detritus, probably coming from the bog and consequently a more abounding aquatic vegetation. The stream at the exit of the pool measures ~ 4 m in width and 50 cm in depth. Downstream from the pool, the vegetation coverage at the banks decreases a bit, which leaves fewer shelters for the frogs. In fact, a lower population density was detected there.
Adults of T. halli were found mainly under the tussocks, where they shared their refugia with other adults and larvae. On one occasion, 11 adults and one tadpole were captured from below the same plant. Tadpoles also exhibit gregarious habits, but somehow seem to prefer to shelter inside the aquatic vegetation, at the bottom of the stream. Still, they are not absent under the cushions at the riverbank. Most of the observed larvae were at approximately the same development stage (Gosner stage 36–37); however, two specimens were younger (Gosner stages 27 and 33). Directly inside the pool, there were very few Telmatobius tadpoles and only one adult was found a few meters below the outlet.
During the daytime, two adults of Rhinella spinulosa were found under the riparian vegetation in the pool and after nightfall, numerous individuals of these toads were observed outside the water along the stream. A small ravine, adjacent to the pool, was occupied by hundreds of Rhinella larvae in semi-lentic, shallow puddles, which are ideal for their development. Additionally, one specimen of Pleurodema marmoratum (Duméril & Bibron, 1840) was found walking around at night; hence, all three potential anuran species were present in the area. Since no case of syntopy between the Chilean Telmatobius has been reported, no other congener is expected to be encountered in Miño.
In the afternoon (05:00 p.m.), the air temperature was 21.8 °C, almost equal to the water temperature at the outlet of the pool (21.4 °C). In contrast, in the morning (8:00 a.m.) the air temperature was -2.4 °C, while water temperatures at the pool and the sampling site were 19.0 °C and 20.7 °C, respectively. After sunset, the air temperature dropped quickly to around -11.0 °C (00:30 a.m.) and remained alike until dawn. The minimum value was -13.1 °C at 03:30 a.m. The water temperature, which is generally higher than that of other localities of the genus (
Overall, T. halli is a medium-sized frog (Table
Morphometrics of adults of Telmatobius halli from Miño. All measurements are expressed in millimeters. Measurements of the holotype (
Adults (n = 11) | |||||
---|---|---|---|---|---|
Variable | Mean | Min | Max | Holotype | Paratype |
SVL | 42.94 | 38.95 | 57.15 | 57.06 | 48.04 |
HW | 13.34 | 11.65 | 19.80 | 18.75 | 16.58 |
HL | 12.76 | 11.00 | 17.80 | 16.50 | 14.27 |
IOD | 4.06 | 3.30 | 5.75 | 6.04 | 4.91 |
IND | 2.87 | 2.20 | 4.20 | 3.65 | 3.03 |
FL | 22.15 | 20.10 | 29.15 | 40.21 | 32.27 |
TL | 18.90 | 17.00 | 21.55 | 24.03 | 20.26 |
Morphometrics of larvae of Telmatobius halli from Miño. All measurements are expressed in millimeters; TTL = total length, BL = body length.
Tadpoles (n = 9) | |||
---|---|---|---|
Gosner stage | n | TTL (Mean) | BL (Mean) |
27 | 1 | 58.35 | 24.00 |
33 | 1 | 97.95 | 30.75 |
36 | 5 | 97.38 | 38.39 |
37 | 2 | 97.00 | 39.10 |
Adults from the three known populations of Telmatobius halli, as recognized in this study, showing the similarity in their external appearance A Miño B Las Cascadas and C Vilama River. The inlay in the upper right corner of C shows a detail of the keratinous spines. Photograph credits for the Vilama River specimen: Felipe Rabanal. Scale bars: 1 cm.
We obtained final alignments of 568 nucleotide sites for the fragment 16S and of 975 for the cytb. However, both alignments were incomplete because the sequences of several specimens included from previous studies are shorter, particularly some fragments of the cytb of the T. marmoratus group from
Bayesian consensus tree (50% majority-rule; mitochondrial genes concatenated, treated as two separated partitions), showing the relationships among Chilean Telmatobius and the species groups recovered by
Phenotypic similarities and differences between T. halli, T. dankoi, and T. vilamensis. Bold font indicates diagnostic characters. Numbers in parentheses specify the source of the information: (1)
Trait | T. halli | T. dankoi | T. vilamensis |
---|---|---|---|
Dentition | vomerine teeth absent (1) | vomerine, premaxillary, and maxillary teeth absent (2, 3) | vomerine, premaxillary and maxillary teeth absent (5) |
maxillary teeth rudimentary [0.2–0.3 mm], only present on the upper jaw (1) | – | teeth present in some individuals (6) | |
premaxillary teeth absent, maxillary teeth rudimentary (5) | – | – | |
Skin | smooth (1, 5, 7) | smooth dorsal and ventral skin (2) | smooth; flanks, chest, throat, and ventral surfaces of the arms without keratinous spines (5) |
few granules on dorsum and the posterior surfaces of the thigh, more prominent around and below the vent (1) | small keratinous spines on head, flanks, posterior third of the dorsum and extremities [both sexes] (3) | numerous, minute, transparent or white spines on the venter and the ventral surface of the extremities (5) | |
flanks, extremities and posterior dorsum with minute granules and dark keratinous spines; the extension of this trait is highly variable (7) | minute dark spines irregularly distributed on flanks, throat and anterior extremities (5) | dark spines on flanks, extremities and posterior dorsum (7) | |
Postfemoral fold | absent (5) | wide; well-developed (3) | present but smaller (5) |
present; variable in size (7) | – | well-developed in holotype (5) | |
Snout (dorsal view) | truncated (5) | rounded or pointed (5) | rounded or prominently pointed (5) |
varies between truncated and slightly pointed (7) | – | acuminate (4) | |
Snout (lateral view) | flat (1) | pointed, depressed (2) | strongly depressed (5) |
moderately short in lateral view (5) | not depressed (5) | projected distally (4) | |
varies between flat and rounded and short and acuminate (7) | – | – | |
Webbing | toes webbed to the tips but so emarginate that they appear only half webbed (1, 7) | not mentioned, but the illustration of the holotype shows a well-developed webbing that ends in fringes toward the tips (fig. 3F of |
wide fringes (4) |
toes extensively webbed, outer border of Toe V widely fringed (5) | – | toes webbed; outer border of Toe V moderately fringed (5) | |
size of the fringes variable (7) | – | – | |
Tongue | oval, entire, two-thirds the width of mouth at its greatest transverse diameter (1) | elliptical (2) | nearly ovoid, elongate, almost adhered to the floor of mouth, posterior border free (5) |
completely attached to the floor of the mouth (2) | rounded (5) | – | |
round, thick; with posterior border free, unnotched; slightly longer than wide; attached through more than 75% of its length (5) | – | – | |
Tympanum | tympanum absent (1, 5) | tympanum and tympanic annulus absent (5) | tympanum and tympanic annulus absent (5) |
tympanic annulus absent (5) | – | – | |
Cranial osteology | choanae large, subrectangular (5) | cranium well-ossified (5) | cranium poorly ossified (5) |
– | vomer absent (3) | vomers rudimentary or absent (5) | |
– | columella absent (3) | columella absent (5) | |
– | – | choanae large, circular (5) | |
– | – | neopalantines reduced (5) | |
Tadpoles | long pointed tails; the distal third or two-fifths [of the dorsal fin] is thickly spotted with dark brown (1) | rounded tail end (2) | tail tip rounded (5) |
– | end of tail pointed (3) | myomeres and fins with irregular, dark brown spots (5) | |
– | uniformly pigmented tail (2) | – | |
– | distal tip of the tail black [posterior third] (3) | – | |
– | presence of black tip is variable (7) | – | |
Tibio-tarsal joint carried forward | extends to the posterior margin of the eye (1) | does not reach the posterior border of the eye (3) | reaches or exceeds the posterior border of eye (5) |
reaches the anterior border of the eye (3) | reaches or exceeds the posterior border of eye (5) | – |
The rudimentary nature of the maxillary teeth of T. halli was one of the features that motivated the description of the species. Since we did not examine the dentition of the frogs from Miño, an evaluation of this issue remains pending. At first glance this point seems decisive, adding the fact that the absence of teeth is also listed as an important trait in the diagnoses of T. dankoi and T. vilamensis. Nevertheless,
Telmatobius dankoi was distinguished by having small keratinous spines on the head, flanks, posterior third of the dorsum and extremities in both sexes (
Another feature on which emphasis was made in the descriptions of T. dankoi and T. vilamensis is the presence of postfemoral folds. Both species differ from their congeners by presenting well-developed folds, although it was reported that these are smaller and thinner in T. vilamensis (
In the case of T. vilamensis, the shape of the snout was stated as an outstanding character and is described as being “strongly depressed” (
Almost half of the diagnostic characters of T. vilamensis are cranial bone structures, which contrasts with the diagnoses of T. halli and T. dankoi, where few osteological characters were included. Therefore, from an osteological point of view, there are not many elements to compare the three populations. Some of the aforementioned osteological features have been attributed to immature stages of post-metamorphic development in T. dankoi and T. vilamensis, in comparison to other species of the genus (
The development of webbing and fringes on the toes has been included in the diagnoses of T. halli and T. vilamensis (
With respect to the tadpoles,
One particular character was not included in the diagnosis of any of the three species, but was used to differentiate T. dankoi from its Chilean congeners (
The usefulness of three additional characters that appear in the diagnoses can be discarded. Body size was included in the diagnosis of T. dankoi (SVL = 49.7–51.7 mm,
In summary, considering all the available information, in the literature there are two contrasting views on morphological variation among T. halli, T. dankoi, and T. vilamensis. On the one hand, there are two studies where the limits of T. halli are broadened: one that adds the population of Arroyo Vilama (
Therefore, the external, osteological, and ecological characteristics as a whole do not allow to clearly distinguish T. halli, T. dankoi, and T. vilamensis, and the described variation of some morphological characters can be interpreted as intra- and interpopulation polymorphisms between the three known populations. Bearing in mind also their indistinguishable mitochondrial sequences and their high genetic affinity detected with microsatellite markers (
The discovery of a Telmatobius population at the origin of the Loa River (Miño) definitely solves one of the most persistent enigmas of Chilean herpetology: the location of the population originally described as T. halli. This riddle persisted for more than eighty years because of the uncritical acceptance of the inherently vague description of the type locality by
The Loa River at Miño has an almost constant water temperature of around 20 °C, even at prolonged ambient temperatures below the freezing point, which suggests geothermal activity and matches well with the literature on the type locality of T. halli (
We were able to verify on the ground two other conditions defined by
The elevation of the type locality of T. halli is one of the problematic aspects of the description provided by
The fifth condition of
In the chronicles of the IHAEC, there is little information about the population of Telmatobius from Miño.
This is the first study to include the population that was originally described as T. halli in a phylogenetic analysis. Although this analysis was performed only with mitochondrial sequences (nuclear markers have not yet been included in phylogenetic analyses of the genus), it included all Chilean species of the genus and all known populations that are geographically close. Telmatobius halli formed a highly supported clade with the two endemic species from the extreme south of the genus distribution in Chile, T. dankoi and T. vilamensis, both of which had previously been considered T. halli (e.g.,
The possible synonymy between T. dankoi and T. vilamensis had already been pointed out by
The conspecificity of these three species also has important consequences for the conservation of these populations due to the current critical situation of the populations previously assigned to T. dankoi and T. vilamensis. In 2019, the only stream from where T. dankoi was known (Las Cascadas) almost completely dried up, resulting in the loss of approximately 90% of the total population (
Currently, based on the scarce and incomplete information available for this species, T. halli is listed as Data Deficient by the IUCN (
Up until now, there seems to exist very little anthropic disturbance at the location described in this work and the place appears to be visited only occasionally by anglers, off-road enthusiasts, and mountaineers. Since the times of the IHAEC, it has been a recreational area mainly for the mine staff and, according to locals, still in the 1990s, the spot was sporadically visited by workers from the nearby mines. Accessing the site is very difficult and an increase in tourist activity is unlikely to happen. The valley is very pristine with no visible pollution signs. There is a vehicular track, that crosses the riverbed, which means that there could occur an occasional roadkill or minor contamination with motor oil or fuel; however, given the remoteness of the location not many vehicles pass through. Furthermore, it has yet to be evaluated if the intense nearby mining activity at the Collahuasi and Quebrada Blanca copper mines poses an imminent threat to the Telmatobius population, for instance, if contamination with heavy metals could occur through industrial dust dispersion (e.g.,
As mentioned above, other species of Telmatobius have been found infected with Batrachochytrium dendrobatidis (Bd) in northernmost Chile and there is an ongoing spread of chytridiomycosis southwards the Andes (
Introduced salmonids are another threat for native amphibians in Chile (
Besides these anthropic influences, it is also necessary to consider natural factors that could constitute a threat to the population. The extreme north of Chile is affected by intense precipitations during the so-called Altiplanic winter, which generates flash floods and landslides, having a negative impact on the biota. This phenomenon significantly reduces the riparian vegetation (
All these threats, alone or in combination, could potentially lead to the extinction of T. halli. Therein lies the importance of protecting the upper portion of the Loa River, where the watercourse and the surroundings are seemingly untouched for several kilometers. As a next step, surveys to determine the presence of Telmatobius along the river and its tributaries should be organized.
Special thanks to Ben von Tschirnhaus for his invaluable support during the fieldwork. We also thank Bill Stolz from the Special Collections and Archives at the Wright State University Libraries for providing the digitization of Ross McFarland’s legacy. The reproduction of this visual material was kindly authorized by Wright State University Libraries’ Special Collections and Archives. Lastly, we thank Felipe Rabanal for allowing us to use his photography of the individual from Vilama River and for his observations of that individual.
Specimens of Telmatobius included in the phylogenetic analyses. For each specimen, species, locality (country), collection number or label, GenBank accession number (for each DNA fragment) and source of the sequences are indicated. Identification of specimens follows the taxonomy prior to
Species | Locality | Collection number or label | cytb | 16S | Source |
---|---|---|---|---|---|
T. culeus | Lago Titicaca (Bolivia) | MNCN 43590 | GU060589 | GU060554 | |
T. gigas | Huayllamarca (Bolivia) | CBF 3962 (cytb) / CBF 3964 (16S) | GU060593 | GU060558 | |
T. marmoratus | Laguna Macaya (Bolivia) | MNCN 43513 | GU060600 | GU060565 | |
T. marmoratus | Isluga (Chile) | DBGUCH 0604027 | KJ562938 | KJ563008 |
|
T. marmoratus | Isluga (Chile) | DBGUCH 0604047 | KJ562939 | KJ563009 |
|
T. marmoratus | Río Pacokhaua (Bolivia) | MNCN 43542 | GU060602 | GU060567 | |
T. marmoratus | Quebrada Tana (Chile) | DBGUCH 0910010 | KJ562944 | KJ563014 |
|
T. marmoratus | Quebrada Tana (Chile) | DBGUCH 0910011 | KJ562945 | KJ563015 |
|
T. marmoratus | Quebrada Tana (Chile) | DBGUCH 0910012 | KJ562946 | KJ563016 |
|
T. marmoratus | Quebrada Tana (Chile) | DBGUCH 0910013 | KJ562947 | KJ563017 |
|
T. marmoratus | Quebe (Chile) | DBGUCH 0704034 | KJ562941 | KJ563011 |
|
T. marmoratus | Quebe (Chile) | DBGUCH 0801051 | KJ562942 | KJ563012 |
|
T. marmoratus | Quebe (Chile) | DBGUCH 0812020 | KJ562943 | KJ563013 |
|
T. marmoratus | 8 km N Comanche (Bolivia) | MNCN 43608 | GU060603 | GU060568 | |
T. marmoratus | La Cumbre (Bolivia) | MNCN 43585 | GU060605 | GU060570 | |
T. marmoratus | Zongo (Bolivia) | Unassigned CBF | GU060607 | GU060572 | |
T. marmoratus | Colpa (Chile) | DBGUCH 0801007 | KJ562896 | KJ562971 |
|
T. marmoratus | Colpa (Chile) | DBGUCH 0801008 | KJ562897 | KJ562972 |
|
T. marmoratus | 7 km Charazani (Bolivia) | Unassigned CBF | GU060608 | GU060573 | |
T. marmoratus | Río Wasawayq’o (Bolivia) | Unassigned CBF | GU060610 | GU060575 | |
T. marmoratus | Río Charazani (Bolivia) | Unassigned CBF | GU060609 | GU060574 | |
T. marmoratus | Charazani-Escoma (Bolivia) | Unassigned CBF | GU060611 | GU060576 | |
T. marmoratus | Kkota Pata (Bolivia) | Unassigned CBF | GU060612 | GU060577 | |
T. marmoratus | Cancosa (Chile) | DBGUCH 0801038 | KJ562889 | KJ562964 |
|
T. marmoratus | Cancosa (Chile) | DBGUCH 0801039 | KJ562890 | KJ562965 |
|
T. marmoratus | Caquena (Chile) | DBGUCH 3359 | KJ562891 | KJ562966 |
|
T. marmoratus | Lauca (Chile) | DBGUCH 0811013 | KJ562892 | KJ562967 |
|
T. marmoratus | Lauca (Chile) | DBGUCH 0811020 | KJ562893 | KJ562968 |
|
T. marmoratus | Chungará (Chile) | DBGUCH 3358 | KJ562894 | KJ562969 |
|
T. marmoratus | Parinacota (Chile) | DBGUCH 0704060 | KJ562895 | KJ562970 |
|
T. marmoratus | Putre (Chile) | DBGUCH 0811028 | KJ562898 | KJ562973 |
|
T. marmoratus | Putre (Chile) | DBGUCH 0811032 | KJ562899 | KJ562974 |
|
T. marmoratus | Putre (Chile) | DBGUCH 0811033 | KJ562900 | KJ562975 |
|
T. hintoni | Corani (Bolivia) | MNK A959 | GU060594 | GU060558 | |
T. hintoni | Tunari (Bolivia) | Unassigned CBF | GU060596 | GU060561 | |
T. huayra | Pastos Grandes (Bolivia) | MNCN 43564 (cytb) / MNCN 43565 (16S) | GU060599 | GU060563 | |
T. fronteriensis | Puquios (Chile) | DBGUCH 1110029 | KJ562884 | KJ562959 |
|
T. fronteriensis | Puquios (Chile) | DBGUCH 1110031 | KJ562885 | KJ562960 |
|
T. fronteriensis | Puquios (Chile) | DBGUCH 1110032 | KJ562886 | KJ562961 |
|
T. fronteriensis | Puquios (Chile) | DBGUCH 1110034 | KJ562887 | KJ562962 |
|
T. fronteriensis | Puquios (Chile) | DBGUCH 1110057 | KJ562888 | KJ562963 |
|
T. philippii | Quebrada Amincha (Chile) | DBGUCH 1110055 | KJ562901 | KJ562976 |
|
Telmatobius cf. philippii | Salar de Ascotán (Chile) | DBGUCH 0505006 | KJ562912 | KJ562986 |
|
Telmatobius cf. philippii | Salar de Ascotán (Chile) | DBGUCH 0505010 | KJ562913 | KJ562987 |
|
Telmatobius cf. philippii | Salar de Ascotán (Chile) | DBGUCH 0505011 | KJ562914 | KJ562988 |
|
Telmatobius cf. philippii | Salar de Carcote (Chile) | DBGUCH 0808015 | KJ562925 | KJ562995 |
|
Telmatobius cf. philippii | Salar de Carcote (Chile) | DBGUCH 0808016 | KJ562926 | KJ562996 |
|
Telmatobius cf. philippii | Salar de Carcote (Chile) | DBGUCH 1109002 | KJ562927 | KJ562997 |
|
Telmatobius cf. philippii | Salar de Carcote (Chile) | DBGUCH 1109003 | KJ562928 | KJ562998 |
|
Telmatobius cf. philippii | Salar de Carcote (Chile) | DBGUCH 1109004 | KJ562929 | KJ562999 |
|
T. chusmisensis | Chusmiza (Chile) | DBGUCH 0812025 | KJ562873 | KJ562952 |
|
T. chusmisensis | Chusmiza (Chile) | DBGUCH 0812026 | KJ562874 | KJ562953 |
|
T. chusmisensis | Laonzana (Chile) | DBGUCH 1111004 | KJ562919 | KJ562989 |
|
T. chusmisensis | Laonzana (Chile) | DBGUCH 1111015 | KJ562922 | KJ562992 |
|
T. chusmisensis | Chusmiza (Chile) | DBGUCH 1111027 | KJ562875 | KJ562954 |
|
T. chusmisensis | Laonzana (Chile) | DBGUCH 1111005 | KJ562920 | KJ562990 |
|
T. chusmisensis | Laonzana (Chile) | DBGUCH 1111012 | KJ562921 | KJ562991 |
|
T. chusmisensis | Salar de Huasco (Chile) | DBGUCH 0704005 | KJ562935 | KJ563005 |
|
T. chusmisensis | Salar de Huasco (Chile) | DBGUCH 0808001 | KJ562936 | KJ563006 |
|
T. chusmisensis | Salar de Huasco (Chile) | DBGUCH 0808002 | KJ562937 | KJ563007 |
|
T. chusmisensis | Piga (Chile) | DBGUCH 0801024 | KJ562940 | KJ563010 |
|
T. chusmisensis | Quebrada Chiclla (Chile) | DBGUCH 0703005 | KJ562930 | KJ563000 |
|
T. chusmisensis | Copaquire (Chile) | DBGUCH 0703003 | KJ562931 | KJ563001 |
|
T. chusmisensis | Copaquire (Chile) | DBGUCH 0703004 | KJ562932 | KJ563002 |
|
T. chusmisensis | Copaquire (Chile) | DBGUCH 1109005 | KJ562933 | KJ563003 |
|
T. chusmisensis | Copaquire (Chile) | DBGUCH 1109006 | KJ562934 | KJ563004 |
|
T. dankoi | Las Cascadas (Chile) | DBGUCH 1108005 | KJ562880 | KJ562955 |
|
T. dankoi | Las Cascadas (Chile) | DBGUCH 1108011 | KJ562881 | KJ562956 |
|
T. dankoi | Las Cascadas (Chile) | DBGUCH 1110015 | KJ562882 | KJ562957 |
|
T. dankoi | Las Cascadas (Chile) | DBGUCH 1110016 | KJ562883 | KJ562958 |
|
T. vilamensis | Río Vilama (Chile) | DBGUCH 3080 | KJ562902 | KJ562977 |
|
T. vilamensis | Río Vilama (Chile) | DBGUCH 1108016 | KJ562903 | KJ562978 |
|
T. vilamensis | Río Vilama (Chile) | DBGUCH 1108018 | KJ562904 | KJ562979 |
|
T. vilamensis | Río Vilama (Chile) | DBGUCH 1108019 | KJ562905 | KJ562980 |
|
T. vilamensis | Río Vilama (Chile) | DBGUCH 1108022 | KJ562906 | KJ562981 |
|
T. halli | Miño (Chile) | L1 | OL412556 | OL412559 | This study |
T. halli | Miño (Chile) | L2 | OL412557 | OL412560 | This study |
T. halli | Miño (Chile) | L3 | OL412558 | OL412561 | This study |
T. pefauri | Zapahuira (Chile) | DBGUCH 3382 | KJ562908 | KJ562982 |
|
T. pefauri | Zapahuira (Chile) | DBGUCH 0504006 | KJ562909 | KJ562983 |
|
T. pefauri | Zapahuira (Chile) | DBGUCH 0504015 | KJ562910 | KJ562984 |
|
T. pefauri | Zapahuira (Chile) | DBGUCH 0606003 | KJ562911 | KJ562985 |
|
T. pefauri | Belén (Chile) | DBGUCH 0811042 | KJ562923 | KJ562993 |
|
T. pefauri | Belén (Chile) | DBGUCH 0811043 | KJ562924 | KJ562994 |
|
T. sibiricus | Siberia (Bolivia) | MNK A965 | GU060615 | GU060580 |
Video S1. Warm springs swimming bath at source of Río Loa in Chile, 1935.
Data type: Video file
Explanation note: Footage taken by Ross McFarland during the International High Altitude Expedition to Chile in 1935. The film shows the expedition members on a Sunday trip to the source of the Loa River. On this occasion, Frank Gregory Hall collected the type series of Telmatobius halli. The video is courtesy of Wright State University Libraries' Special Collections & Archives.