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We describe Allophryne resplendens, a new species from two localities in the Amazon rain-forest of Loreto, Peru, of the family Allophrynidae, which was monotypic until this discovery. The new species can be readily differentiated from Allophryne ruthveni on the basis of dorsal and ventral coloration both in life and in preservative, transverse processes of presacral II ori-ented anterolaterally (oriented laterally in A. ruthveni), 19 nucleotide autapomorphies for 761 base pairs (bp) of the mitochondrial gene 16S, and 16 for 923 bp of 12S. Maximum parsimony analysis of the mitochondrial gene 12S and a fragment of up to 1060 bp of 16S supports the new species as sister to A. ruthveni.
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Copyright © American Museum of Natural History 2012 ISSN 0003-0082
AMERICAN MUSEUM NOVITATES
Number 3739, 17 pp. March 9, 2012
A Second Species of the Family Allophrynidae
(Amphibia: Anura)
SANTIAGO CASTROVIEJOFISHER, PEDRO E. PÉREZPEÑA, JOSE M. PADIAL,
AND JUAN M. GUAYASAMIN
ABSTRACT
We describe Allophryne resplendens, a new species from two localities in the Amazon rain-
forest of Loreto, Peru, of the family Allophrynidae, which was monotypic until this discovery.
e new species can be readily dierentiated from Allophryne ruthveni on the basis of dorsal
and ventral coloration both in life and in preservative, transverse processes of presacral II ori-
ented anterolaterally (oriented laterally in A. ruthveni), 19 nucleotide autapomorphies for 761
base pairs (bp) of the mitochondrial gene 16S, and 16 for 923 bp of 12S. Maximum parsimony
analysis of the mitochondrial gene 12S and a fragment of up to 1060 bp of 16S supports the
new species as sister to A. ruthveni.
INTRODUCTION
Discoveries and new descriptions of amphibian species have increased in recent years, with
the number of nominal species growing of about 48.2% since 1985 (Frost et al., 2006) and
19.4% during the last decade (Köhler et al., 2005). e bulk of these new discoveries arise from
applying recently developed advances in elds such as molecular biology, bioacoustics, and
geography to clades from tropical regions (e.g., Meegaskumbura et al., 2002; Stuart et al., 2006;
Fouquet et al., 2007; Vieites et al., 2009). Discovery of new species is, however, not randomly
1 Division of Vertebrate Zoology (Department of Herpetology), American Museum of Natural History.
2 Wildlife Conservation Society, Programa Loreto, Perú.
3 Centro de Investigación de la Biodiversidad y Cambio Climático, Universidad Tecnológica Indoamérica, Av.
Machala y Sabanilla, Quito, Ecuador.
2 AMERICAN MUSEUM NOVITATES NO. 3739
distributed across clades of amphibians. Some groups account for most of the newly described
diversity (e.g., Ranidae alone includes 25% of the new species of amphibians described since
2004: AmphibiaWeb, 2011) whereas for other groups it may be decades before a second species
within a genus is discovered. For example, Rhinatrema bivittatum (Guérin-Méneville, 1838)
remained as the only known species of Rhinatrema Duméril and Bribon, 1841, for 169 years
until Gower et al. (2010) described a new species, although that discovery was quickly followed
by another (Wilkinson and Gower, 2010).
Allophryne ruthveni Gaige, 1926, has stood as the only member of this monotypic genus
and the family Allophrynidae for 85 years. It is known to occur in the lowland rainforest of
the Amazon and Orinoco basins, from Venezuela and the Guianas to southwestern Brazil and
probably Bolivia (Frost, 2011). Despite its ample distribution, records are rare and sparse.
Phylogenetically, the relationship Centrolenidae + Allophryne ruthveni is the most accepted
hypothesis, supported by molecular phylogenetics (Austin et al., 2002; Faivovich et al., 2005;
Wiens et al., 2005; Frost et al., 2006; Grant et al., 2006; Guayasamin et al., 2008) and morpho-
logical studies (Duellman, 2001; Burton, 2004; Wiens et al., 2005; but see Fabrezi, 2006). In this
work, we describe the second species in the family Allophrynidae, found in the Amazon rain-
forest of Loreto, Peru.
MATERIALS AND METHODS
N
Frost et al. (2006) placed Allophryne ruthveni in the monotypic subfamily Allophryninae,
within Centrolenidae, whereas Guayasamin et al. (2009) argued to maintain the species in the
monotypic family Allophrynidae. We followed the later arrangement (see Guayasamin et al.,
2009, for argumentation).
T S  M
Specimens were collected in the eld according to approved animal use and care protocols
(Heyer et al., 1994), and euthanized in Xylocaïne solution prior to xation and preservation in
ethanol 70%. Specimens studied are listed in appendix 1. Color characteristics are described
according to digital photographs taken from life specimens in the eld. External morphological
characters were examined under a dissecting microscope. Measurements were taken with digi-
tal calipers on preserved specimens to the nearest 0.01 mm and rounded to 0.1 mm. Variables
measured, as described in Duellman (2001), are as follows: snout-vent length (SVL); head
length; head width; interorbital distance; eye diameter; upper eyelid; tympanum diameter; eye-
nostril distance; distance from anterior margin of eye to tip of snout; internarial distance; eye-
tympanum distance; length of forearm; hand length; nger I length; nger II length; width of
disc of nger III; width of nger III; thigh length; shank length; foot length. Ontogenetic status
was determined by examination of the development of gonads and presence of secondary
sexual characteristics (e.g., vocal slits and sacs). Terminology for webbing is that described by
Savage and Heyer (1967), as modied by Guayasamin et al. (2006). e osteological description
2012 CASTROVIEJOFISHER ET AL.: NEW SPECIES OF ALLOPHRYNIDAE 3
FIG. 1. Photographs of preserved specimens of Allophryne. A–C, Allophryne resplendens, new species, adult
female holotype (SVL = 28.4 mm); D–E, Allophryne ruthveni, adult female, Surinam, AMNH 87687 (SVL =
27.0 mm). Photographs by JMP (A–C) and SCF (D–E).
4 AMERICAN MUSEUM NOVITATES NO. 3739
A
C
B
D
E F
FIG. 2. Photographs of live specimens of Allophryne. A, Allophryne resplendens, n. sp., adult female holotype
(SVL = 28.4 mm); B, A. resplendens, n. sp., specimen not collected, sex and size unknown, topotype; C–D, A.
resplendens, new species, adult male, Quebrada Ungurahue (SVL = 25.0 mm); E–F, A. ruthveni, adult male,
Venezuela, MHNLS 20231 (SVL = 23.5 mm). Photographs by Mark Bowler (A), WCS–Perú (B), William
Lamar (C–D), and SCF (E–F).
was based on X-rays of the holotype; osteological terminology is that of Duellman and Trueb
(1986), Fabrezi (1992, 1993), and Trueb (1973, 1993). Museum acronyms are: American
Museum of Natural History (AMNH), Museo Historia Natural La Salle (MHNLS), and Museo
de Zoología de la Universidad Nacional de la Amazonía Peruana (MZUNAP).
M A
We sequenced the complete mitochondrial gene 12S (962 bp) and a fragment of the gene
16S (1060 bp) from the specimen of Allophryne collected in Loreto, Peru, and three specimens
of A. ruthveni from Delta Amacuro, Venezuela. Genomic DNA was isolated using a standard
phenol-chloroform extraction protocol (Sambrook et al., 1989). e selected markers were
2012 CASTROVIEJOFISHER ET AL.: NEW SPECIES OF ALLOPHRYNIDAE 5
amplied and sequenced using the same primers and PCR conditions as in Guayasamin et al.
(2008) with the addition of primers 16L19 and 16H24 (Heinicke et al., 2007). Sequences from
heavy and light strands were compared to generate a consensus sequence for each specimen
using Sequencher 4.6 (Gene Codes Corp., 2006). We compared these sequences with those
from GenBank for Allophryne ruthveni, as well as representative species of all other Neotropical
families within Hyloidea, according to the taxonomy used in Frost (2011). We used sequences
of Mantella madagascariensis to root phylogenetic trees. GenBank accession codes of all the
sequences studied are provided in appendix 2.
Sequences of each marker were independently aligned in MAFFT (Katoh et al., 2005)
under the E-INS-i option. e resulting multiple sequence alignments (Dryad Repository:
doi:10.5061/dryad.2kp7q7vb) were concatenated and analyzed under the maximum parsimony
criterion (MP) using TNT 1.1, Willi Hennig Society Edition (Golobo et al., 2008) with gaps
as a h character and using the “New Technology search” option at level 100, including secto-
rial searches, ratchet (see Nixon, 1999), dri, and tree fusing (see Golobo, 1999). Bootstrap
support (BS, Felsenstein, 1985) was evaluated through 1000 pseudoreplicates, with 10 RAS
using TBR and 10 trees saved per replication. Uncorrected genetic distances were calculated
from 761 bp of the 16S and 923 of the 12S (maximum length overlapping for all the Allophryne
sequences, Dryad Repository: doi:10.5061/dryad.2kp7q7vb) in PAUP* 4.0b10 (Swoord, 1998).
Allophryne resplendens, new species
Figures 1A–C, 2A–D
Allophryne, sp. nov., Rodríguez and Knell, 2003: 244.
H: MZUNAP-01-605 (eld number PEPP 500), adult female from Lago Preto
(4°2735.0S, 71°45 3.5W; 120 m), Río Yavarí, Provincia Ramon Castilla, Departamento
Loreto, Peru, collected by PEPP in November 2009. When collected, the distal section of the
right hind limb of the specimen was missing; we cut a piece of tissue from the stump for
molecular studies purposes.
R: We are aware of three other records of the new species. One is a noncollected
but photographed adult (g. 2B) found in Lago Preto, Yavarí, Loreto, Peru, in July 2008 (pho-
tographs by anonymous volunteers of Earthwatch and deposited at Wildlife Conservation Soci-
ety, WCS–Perú). e second is reported by Rodríguez and Knell (2003) also from Lago Preto
(4°28S, 71°46W; 90 m), Yavarí, Loreto, Peru. Rodríguez and Knell (2003) cite this specimen
as deposited at the MUSM. However, in a visit to the MUSM in March 2008, we were unable
to locate the specimen or to get a voucher code for it. e third specimen, an adult male (g.
2C, D), was collected on the south bank of Quebrada Hungurahui (4°1442.97S, 74°2136.02W;
114 m), an auent of Río Tigre, approximately 2 km north of Comunidad Monteverde, Loreto,
Peru, by William Lamar on 1 August 2006. is specimen was collected and preserved in etha-
nol; unfortunately, the jar did not seal properly and the specimen totally decomposed and
could not be used as a type.
G P: e new species is assigned to the genus Allophryne because of the
following combination of morphological characters: absence of metacarpal III process (its pres-
6 AMERICAN MUSEUM NOVITATES NO. 3739
ence is a synapomorphy of centrolenid frogs), T-shaped terminal phalanges, tibiale and bulare
not fused, absence of neopalatines and quadratojugals, and protruding snout in lateral view;
no phenotypic autoapomorphy is known for the genus. e molecular phylogeny also supports
the placement of the new species in the genus Allophryne. e 10 most parsimonious trees (tree
cost = 11,381 steps) resulting from 100 replicates (each including RAS + TBR + dri and tree
fusing with the best tree hit 100 times) placed Allophryne resplendens, n. sp., as the sister spe-
cies of Allophryne ruthveni (BS = 100; g. 3).
D: Allophryne resplendens, n. sp., is distinguished from A. ruthveni, the only other
known species in the genus and family (character states of the latter are in parentheses), by (1)
color pattern (cf. photos in gs. 1 and 2): dorsolateral surfaces in life black (cream to light
brown) with large and bright glossy spots due to accumulation of iridophores (absent), most
of which containing irregular yellow blotches (absent), dorsolateral surfaces in preservative
dark brown (cream to light brown with dark brown stripes) with large and bright glossy spots
due to accumulation of iridophores (absent), ventral surfaces in life black and opaque (not
pigmented, translucent) with large and bright glossy spots due to accumulation of iridophores
except in palms and plantar surfaces (absent or just a few o-white spots on the throat/chest
and distal parts of legs), same character states for both species for ventral surfaces in preserva-
tive than in life, but coloration dark brown instead of black for A. resplendens; (2) osteology:
transverse processes of presacral II oriented anterolaterally (oriented laterally; observed in two
cleared and stained specimens; see appendix 1, and g. 2C in Fabrezi and Langone, 2000); and
(3) DNA sequences: uncorrected genetic distance > 2.5 % for 761 bp of mitochondrial gene
16S, and ≥ 1.7 % for 923 bp of 12S (table 1), 19 nucleotide autapomorphies for 761 bp of 16S,
and 16 for 923 bp of 12S (table 2).
D   H: Adult female, SVL 28.4 mm. Head wider than long (HL
= 85.7% of HW); snout protruding in lateral prole and broadly rounded in dorsal view (g.
1A, C); canthus rostralis indistinct, straight; loreal region at; lips not ared; nostril small, not
protuberant, closer to tip of snout than to eye. Eye of moderate size (ED = 10.6% of SVL).
Tympanic membrane and tympanic annulus dierentiated; tympanum relatively small (TD =
TABLE 1. Uncorrected genetic distances between specimens of Allophryne inferred from 923 bp of the mitochondrial genes
12S (above the diagonal) and 761 bp of the 16S (below the diagonal). Dryad Repository: doi:10.5061/dryad.2kp7q7vb.
12345678
1 A. resplendens * 2.0% 2.1% 1.7% 2.1% – 2.1%
2 A. ruthveni 3301 2.6% * 0.1% 0.3% 0.1% – 0.1%
3 A. ruthveni 3302 2.6% 0.0% * 0.2% 0.0% – 0.0%
4 A. ruthveni 3303 3.0% 0.7% 0.7% * 0.2% – 0.2%
5 A. ruthveni AY843564 2.9% 0.5% 0.5% 0.9% * 0.0%
6 A. ruthveni EU662973 2.9% 0.4% 0.4% 1.1% 0.4% *
7 A. ruthveni AF364512 3.4% 0.9% 0.9% 1.4% 1.5% 1.4% *
8 A. ruthveni AY819328 – – – – – – – *
2012 CASTROVIEJOFISHER ET AL.: NEW SPECIES OF ALLOPHRYNIDAE 7
Marker Position A. ruthveni A. resplendens
16S 91 G A
92 T C
101 G A
153 T C
174 C T
240 T C
280 A
282 A T
333 –/T C
342 T G
464 A G
542 C T
544 T C
558 A G
584 T C
604 A C
624 T C
628 T C
638 A T
12S 59 T C
91 A G
299 G A
341 T C
370 T C
375 T C
390 T C
459 T/- C
583 A G
625 A T
724 G A
748 C T
851 T C
852 T C
861 T C
922 A G
TABLE 2. Autapomorphies for Allophryne resplendens new species with respect to A. ruthveni inferred from a fragment of
761 bp and 923 bp of the mitochondrial genes 16S and 12S respectively. Dryad Repository: doi:10.5061/dryad.2kp7q7vb.
8 AMERICAN MUSEUM NOVITATES NO. 3739
Allophryne ruthveni AF364512
Allophryne ruthveni MHNLS 20233
Allophryne ruthveni MHNLS 20232
Allophryne ruthveni MHNLS 20231
Allophryne ruthveni AY819328
Allophryne ruthveni EU662973
Allophryne ruthveni AY843564
Allophryne resplendens
Mantella madagascariensis
Hypsiboas geographicus
Bro meliohyla bromeliacia
Anotheca spinosa
Duellmanohyla soralia
Hyloscirtus charazani
Osteocephalus taurinus
Ecnomiohyla miotympanum
Isthmohyla rivularis
Bokermannohyla martinsi
Argenteohyla siem ersi
Charadrahyla taeniopus
Aparasphenodon brunoi
Pristimantis galdi
Yunganastes pluvicanorus
Pri stimantis diadematus
Oreobates cruralis
Lynchius avomaculatus
Stefania schuberti
Gastrothecassipes
Dendrobates auratus
Ameerega trivittata
Silverstoneia otator
Epipedobates t ricol or
Rheobates palmatus
Allobates ta lamancae
Rhaebo nasicus
Dendrophryniscus minutus
Atelopus peruensis
Rhinella arenarum
Atelognathus patagonicus
Telmatobius sp.
Batrachyla leptopus
Ceratophrys cranwelli
Lepidobatrachus sp.
Eupsophus calcaratus
Alsod es ga rgola
Leptodactylus ocellatus
Lithodytes lineatus
Chimerella mariaelenae
Celsiella revocata
Vitreorana gorzul ae
Hyalinobatrachium taylori
Cochranella nola
Centrolene savagei
Teratohyla pulverata
Rulyrana spiculata
Nymphargus bejaranoi
Sachatamia albomaculata
Espadarana andina
Ikakogi ta yrona
Hyla arborea
Paratelmatobius po ecilogaster
Scythrophrys sawayae
Terrarana
Hemiphractidae
Bufonidae
Dendrobatoidea
Hylidae
Ceratophryidae
Cycloramphidae
Allophrynidae
Centrolenidae
Leptodactylidae
100
99
100
81
97
100
100
99
99 98
74
99
99
98
74
98
99
97
98
76
98 98
95 77
100 87
FIG. 3. Strict consensus of the 10 most parsimonious trees inferred from 12S and 16S sequences (tree cost =
11,381 steps). Bootstrap support values are indicated above branches when ≥ 70.
2012 CASTROVIEJOFISHER ET AL.: NEW SPECIES OF ALLOPHRYNIDAE 9
FIG. 4. X-ray of the holotype of Allophryne resplendens, n. sp. Arrow points to the anterolaterally oriented
transverse processes of presacral II.
3.9% of SVL). Dentigerous process of vomer indistinguishable. Ulnar tubercles absent; relative
lengths of ngers: III > IV > II > I webbing on hands basal. Discs expanded, truncate; subar-
ticular tubercles round, conspicuous; few supernumerary tubercles; palmar tubercle oval, sim-
ple. Posterior limbs relatively long (FL = 40.8% of SVL; TL = 43.3% of SVL); tarsal tubercles
absent; feet about 3/4 webbed, formula: I 0+–2 II 1–2 III 1–2 IV 3–2 V; discs on toes ellipti-
cal; inner metatarsal tubercle ovoid; outer metatarsal tubercle small, barely evident; subarticu-
lar tubercles round, conspicuous; supernumerary tubercles absent. Skin on dorsal surfaces of
head and body shagreen with hemispherical pustules having a central spicules; venter areolate.
Cloacal opening directed posteriorly at midlevel of thighs, covered by a slightly developed
cloacal sheath; cloacal tubercles absent.
C  L: is description is based on photographs of the holotype and the other
three mentioned specimens (g. 2; Rodríguez and Knell, 2003: g. 5C). Dorsolateral surfaces
with large and bright glossy spots due to accumulation of iridophores, most of which contain
yellow irregular blotches, set in a washed black reticulum; reticulum carries smaller and less
bright oval to pentagon-shaped accumulations of iridophores from which brown spicules arise.
10 AMERICAN MUSEUM NOVITATES NO. 3739
Ventral surfaces black and
opaque with large and bright
glossy spots due to accumula-
tion of iridophores except in
palms and plantar surfaces.
Iris dark bronze with dark
reticulations, pupillary ring
absent, pupil black. There
seems to be sexual dichroma-
tism; the female has fewer
spicules and more ventral
glossy spots than the male,
which is also the case in
Allophryne ruthveni.
C  P:
This description is based
exclusively on the holotype
(g. 1A–C). Dorsolateral sur-
faces with white large and
bright irregular spots due to
accumulation of iridophores,
yellow irregular blotches
absent, set in a dark brown
reticulum that carries smaller
and less bright oval to penta-
gon-shaped accumulations of
iridophores from which brown spicules arise. Ventral surfaces dark brown with large and bright
glossy spots due to accumulation of iridophores except in palms and plantar surfaces. Iris
brown and pupil white.
O (g. 4): e skull is widest posterior to the orbit and at the level of the articula-
tion of the maxilla with the squamosal. e neopalatines and quadratojugals are absent. e
anterior ramus of the pterygoid articulates with the posterior end of the maxilla. e vertebral
column has eight presacral vertebrae that have transverse processes except presacral I. e
vertebral prole in decreasing order of overall width of bony parts is: sacrum > III > IV > V ≈
VI ≈ VII > II > I. e orientations of the transverse processes of presacral VI are lateral,
whereas those of presacrals II, VII, and VIII are anterolateral, and those of presacral III–V are
posterolateral. e bony sacral diapophysis is broadly expanded distally, and has a slender base
that is approximately a third the width of the distal margin. e leading edge of each diapophy-
sis is slightly concave with an anterolateral orientation, whereas the posterior margin is nearly
straight and oriented posterolaterally. e urostyle is slender and shorter than the length of the
presacral portion of the vertebral column; the urostyle bears a dorsal crest on its anterior half.
FIG. 5. Known distribution of Allophryne resplendens, n. sp. Star rep-
resents type locality.
2012 CASTROVIEJOFISHER ET AL.: NEW SPECIES OF ALLOPHRYNIDAE 11
e tibiale and bulare are not fused medially. e phalangeal formulae for the hand and foot
are standard, 2-2-3-3 and 2-2-3-4-3, respectively. In increasing order of length, the order of the
digits on the hand is I < II < IV < III and that of the foot is: I < II < III < V < IV. e terminal
phalanges of hands and feet are T-shaped.
M: e morphometric data for the female holotype are (in mm): SVL = 28.4;
head length = 7.8; head width = 9.1; thigh length = 11.6; shank length = 12.3; foot length =
11.5; interorbital distance = 3.6; upper eyelid width = 2.0; internarial distance = 1.7; eye-to-
nostril distance = 2.5; snout-eye distance = 3.3; eye diameter = 3.0; tympanum diameter = 1.1;
eye-tympanum distance = 1.1; forearm length = 5.7; hand length = 8.7; nger I length = 6.1;
nger II length = 6.5; and width of disc of nger III = 1.6.
D: Allophryne resplendens new species is currently known only from two
localities in Peru (g. 5). e type locality is in the Yavarí River drainage. is drainage includes
other rivers, such as the Yavarí Mirín and Quebrada Esperanza. e region is dominated by
the geological formation that covers much of northeastern Peru: the Pebas formation, a thick
slab of clays and sands deposited in ancient lakes and rivers (Räsaänen et al., 1998; Sánchez et
al., 1999; de la Cruz et al., 1999). e southern sector, close to Angamos, is associated with an
uplied geological structure known as the Iquitos Arch, which stretches hundreds of kilometers
across Loreto and into Colombia. e vegetation of the area includes upland (terra rma) forest
concentrated along the Iquitos Arch, ooded (varzea) forest and palm swamps. e second
known locality is the western side of the Amazon River, Quebrada Hungurahui (an auent of
Río Tigre), approximately 2 km north of Comunidad Monteverde, Loreto, Peru. Allophryne
resplendens, n. sp., is likely present in other varzea forests at least around and between the two
known localities. us, it is possible that this species also occurs in Brazil.
N H: is is an arboreal species that has been found perched on leaves and
branches below 2 m. e holotype was found on a Lepidocaryum tenue (Arecaceae). ese
medium-size palm trees form particular forests known locally as irapayales. e specimen from
Quebrada Hungurahui was also found in an irapayal forest. Allophryne resplendens, n. sp., is
very dicult to nd, which could reect very low densities, at least in the lower strata of the
forest outside the breeding season (the sister species is a explosive breeder). Aer 49.45 hours
of search only one specimen was collected (table 3), and Rodríguez and Knell (2003) found
only a single specimen in 200 hours of search. William Lamar (personal commun.) has visited
the locality in Quebrada Hungurahui during the last 10 years in dierent months and has not
TABLE 3. Search eort distributed by forest type and season in the Yavarí river.
Flooding season (November) Dry season (June–July)
Palm swamps Varzea Terra rma Palm swamps Varzea Terra rma
Search hours 2.5 7.42 12.28 8.75 10.50 8.00
Number of people 2 2 1 2 2 2
Specimens found 1 0 0 0 0 0
12 AMERICAN MUSEUM NOVITATES NO. 3739
been able to locate by sight or sound any other specimens. At least 45 species of amphibians
have been reported from the type locality and surroundings, of which 23 have been found in
swamp palm forest.
E: e specic name resplendens is derived from the Latin verb resplendo mean-
ing “to glitter,” which we used in allusion to the bright and ornate coloration of the frog.
DISCUSSION
T
Monotypic supraspecic taxa can result problematic. For example, dierent Linnean ranks
convey the same information (Allophrynidae = Allophryne = Allophryne ruthveni) and phyloge-
netic denitions are repetitive (see Guayasamin et al.’s [2009] attempt to dene Allophrynidae and
Allophryne). Our discovery of a new species of Allophryne partly solves this problem. Allophryne
is no longer equivalent to the species Allophryne ruthveni and we provide a new phylogenetic de-
nition of the family and genus: a clade stemming from the most recent common ancestor of
Allophryne ruthveni Gaige, 1926, and Allophryne resplendens Castroviejo-Fisher et al., 2011.
P R
Our MP tree shows the sequences of A. resplendens, n. sp., as sister to those of A. ruthveni.
However, the MP analysis does not support the relationship (Leptodactylidae, (Allophrynidae,
Centrolenidae)), which has been suggested in other phylogenetic studies (e.g., Frost et al., 2006;
Guayasamin et al., 2008; Heinicke et al., 2009; Pyron and Wiens, 2011) although with low support.
We explain this lack of resolution by the fact that our dataset was primarily designed to evaluate
whether A. resplendens, n. sp., was more closely related to Allophrynidae than to representatives
of all other families of Neotropical Hyloidea. Our results are therefore not comparable to studies
using much larger taxon and character sampling (e.g., Frost et al., 2006; Pyron and Wiens, 2011).
e unique combination of phenotypic characters exhibited by Allophryne ruthveni has long
puzzled herpetologists, resulting in dierent and conicting phylogenetic hypotheses placing
Allophrynidae as the sister taxon of the families Bufonidae (Gaige, 1926; Laurent, 1980, 1986),
Hylidae (Lynch and Freeman, 1966; Hoogmoed, 1969; Duellman, 1975; Duellman and Trueb,
1986), or Centrolenidae (Noble, 1931; Lutz, 1968; Duellman, 2001; Burton, 2004; Wiens et al.,
2005). Although no unique autapomorphy has been described for A. ruthveni, the following
combination of characters has been proposed as diagnostic: intercalary elements absent, biaxial
articulation between last two phalanges, T-shaped terminal phalanges, tibiale and bulare not
fused, absence of neopalatines and quadratojugals, prepollex and prehallux formed by one proxi-
mal element each (Fabrezi and Langone, 2000, 2001; Fabrezi, 2006). Unfortunately, we have been
able to secure only one specimen of A. resplendens, n. sp., so we could investigate only three of
the characters mentioned above (i.e., T-shaped terminal phalanges, tibiale and bulare not fused,
absence of neopalatines and quadratojugals). e next logical step in the study of Allophryne
would be to gather more information on these and other phenotypic characters and study them
in combination with other relevant information and taxa in a cladistic framework.
2012 CASTROVIEJOFISHER ET AL.: NEW SPECIES OF ALLOPHRYNIDAE 13
ACKNOWLEDGMENTS
We thank Mark Bowler, Miguel Antúnez, Maria Soledad Riveros, Bray Torres, Franco San-
tana, Claudia Rios, Ciro Pinedo, Richard Bodmer, Pablo Puertas, and the volunteers of Earth-
watch Institute for supporting the study in Lago Preto; Juan Carlos Chaparro for his support
and help in the description of this species; and William Lamar for photographs and data on
the new locality. e Wildlife Conservation Society–Perú (WCS–Perú) and AmazonEco pro-
vided nancial support for eldwork. Collection permits in Peru (authorization N° 320-2009)
were issued by AG-DGFFS-DGEFFS. is study is included in the “Contrato Marco de Acceso
a Recursos Genéticos N° 0001, 11 Enero 2007” subscribed between Fundacion La Salle de
Ciencias Naturales and the Ministerio del Ambiente, Venezuela. e work of SCF was nanced
by a Fulbright/Ministry of Education postdoctoral research contract. e Universidad Tec-
nológica Indoamérica supports J.M.G.s research. J.M.P.’s research is funded by a Gerstner Post-
doctoral Fellowship at the American Museum of Natural History.
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16 AMERICAN MUSEUM NOVITATES NO. 3739
APPENDIX 1
A S S
Allophryne ruthveni: VENEZUELA: D A: Reserva Forestal Rio Grande,
Coderforce (08°1600.8N, 61°4516.3W; 192 m), MHNLS 20231–6 (adult males). A:
Base camp of Tapirapeco expedition, upper rio Mavaca (150 m), AMNH 131351 (adult female,
cleared and stained). SURINAM: S: Raleigh Cataracts, Coppename river (50 m),
AMNH 87687 (adult female), 876888 (adult male). GUYANA: I: Pakatau creek,
AMNH 163990 (adult female). Marudi creek, AMNH 44749 (male). U L:
AMNH 70108 (adult female), AMNH 70110 (unknown sex, cleared and stained)
.
APPENDIX 2
S,  T C S  G C, U   S.
Sequences newly generated for this study are in boldface.
Family Genus Species 12S 16S
Allophrynidae Allophr yne resplendens JQ436697 JQ436698
Allophryne ruthveni AY819328 —
Allophryne ruthveni JQ436702 JQ436700
Allophryne ruthveni JQ436703 JQ436699
Allophryne ruthveni JQ436704 JQ436701
Allophryne ruthveni AY843564 AY843564
Allophryne ruthveni — AF364512
Allophryne ruthveni — EU662973
Aromobatidae Allobates talamancae 170026605 170026605
Rheobates palmatus 170026602 170026602
Bufonidae Atelopus peruensis 77176491 77176491
Dendrophryniscus minutus 61697193 61697193
Rhaebo nasicus 77176549 77176549
Rhinella arenarum 61697184 61697184
Centrolenidae Celsiella revocata EU663379 EU663019
Centrolene savagei EU663380 187729151
Chimerella mariaelenae EU663350 EU662991
Cochranella nola EU663375 EU663015
Espadarana andina EU663335 EU662976
Hyalinobatrachium taylori EU663420 EU663056
Ikakogi tayrona EU663358 EU662999
Nymphargus bejaranoi EU663422 EU663059
Rulyrana spiculata EU663382 EU663022
Sachatamia albomaculata EU663362 EU663003
Teratohyla pulverata EU663416 EU663053
2012 CASTROVIEJOFISHER ET AL.: NEW SPECIES OF ALLOPHRYNIDAE 17
Family Genus Species 12S 16S
Vitreorana gorzulae EU663348 EU662989
Ceratophryidae Atelognathus patagonicus 61697182 61697182
Batrachyla leptopus 61697183 61697183
Ceratophrys cranwelli 61697186 61697186
Lepidobatrachus sp 37699560 37699560
Telmatobius sp 61697380 61697380
Cycloramphidae Alsodes gargola 61697176 61697176
Eupsophus calcaratus 61697198 61697198
Dendrobatidae Ameerega trivittata 170026722 170026722
Dendrobates auratus 61697192 61697192
Epipedobates tricolor 37624303 37624303
Silverstoneia otator 170026684 170026684
Hemiphractidae Gastrotheca ssipes 61697203 61697203
Stefania schuberti 61697379 61697379
Hylidae Anotheca spinosa 61697177 61697177
Aparasphenodon brunoi 61697178 61697178
Argentohyla siemersi 61697181 61697181
Bokermannohyla martinsi 61697252 61697252
Bromeliohyla bromeliacia 61697223 61697223
Charadrahyla taeniopus 61697290 61697290
Duellmanohyla soralia 61697195 61697195
Ecnomiohyla miotympanum 61697256 61697256
Hyla arborea 61697212 61697212
Hyloscirtus charazani 61697229 61697229
Hypsiboas geographicus 61697239 61697239
Isthmohyla rivularis 61697270 61697270
Osteocephalus taurinus 61697320 61697320
Leptodactylidae Leptodactylus ocellatus 61697299 61697299
Lithodytes lineatus 37699553 37699553
Paratelmatobius poecilogaster 159139110 159139110
Scythrophrys sawayae 159139126 159139126
Mantellidae Mantella madagascariensis 89255435 89255435
Strabomantidae Lync hius avomaculatus 166155972 166155972
Oreobates cruralis 166155971 166155971
Pristimantis diadematus 166155973 166155973
Pristimantis galdi 166155975 166155975
Yunganastes pluvicanorus 61697197 61697197
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is paper meets the requirements of ANSI/NISO Z39.48-1992 (permanence of paper).
... The genus Allophryne was proposed to accommodate the monotypic species Allophryne ruthveni Gaige, 1926 from Amazonian Guyana. Two other Allophryne species were described as recent as in the 2010s: A. resplendens Castroviejo-Fisher, Pérez-Peña, Padial &Guayasamin, 2012 andA. relicta Caramaschi, Orrico, Faivovich, Dias &Solé, 2013. ...
... The genus Allophryne was proposed to accommodate the monotypic species Allophryne ruthveni Gaige, 1926 from Amazonian Guyana. Two other Allophryne species were described as recent as in the 2010s: A. resplendens Castroviejo-Fisher, Pérez-Peña, Padial &Guayasamin, 2012 andA. relicta Caramaschi, Orrico, Faivovich, Dias &Solé, 2013. ...
... Individuals of Allophryne resplendens were identified in the field by its distinctive color pattern consisting of bright yellow blotches on a black background (Castroviejo-Fisher et al. 2012; Fig. 1). Along an 800 m trail, at least 30 calling males of A. resplendens were found in an explosive breeding event that lasted a couple of days in a flooded forest after heavy rains. ...
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A total of 149 ant species from 35 genera and 10 subfamilies have been identified from the collections made during the 2012 RAP survey of Southeastern Suriname. Additional work is ongoing to process and identify the remaining samples, which will undoubtedly raise the total number of species, possibly to over 200 species. The results indicate a healthy and diverse ant fauna reflective of pristine rainforest. Ants play important roles as predators, scavengers, and seed-dispersers in tropical forests. The ant data from Southeastern Suriname will add to a growing dataset on the ant ant fauna of the Guiana Shield, which is still poorly documented, to help identify areas of high diversity and endemism that are important to conserve within the region. Data on ants and other invertebrates are important since these groups may be able to illustrate differences between habitats within the Guiana Shield that larger animals with wide geographical ranges do not discern. INTRODUCTION With over 12,000 described species of ants in the world (see AntWeb), and their social lifestyle consisting of colonies ranging in size from just a few to millions of workers, ants are a dominant force in all terrestrial ecosystems, especially tropical rainforests. They are important members of the ecosystem, with high biomass and population size, and provide key ecological functions such as aerating and turning soil, dispersing plant seeds, consuming dead animals, and controlling pest insects. In addition to their ecological importance, ants have several features that make them especially useful for conservation planning, including: 1) they are dominant members of most terrestrial environments, 2) they are easily sampled in sufficiently high numbers for statistical analysis in short periods of time (Agosti et al. 2000), 3) they are sensitive to environmental change (Kaspari and Majer 2000), and 4) they are indicators of ecosystem health and of the presence of other organisms, due to their numerous symbioses with plants and animals (Alonso 2000). Ants have been poorly surveyed in Suriname. After the 2005 RAP survey of the Lely and Nassau Mountains (Sosa Calvo 2007) and the 2010 RAP survey in the Kwamalasamutu region of SW Suriname (Alonso 2011), a conservative estimate of about 370 ant species had been recorded in Suriname. However, given the low effort of ant sampling in Suriname and the few localities sampled, there are likely many more ant species in the country. METHODS Ants were surveyed at RAP Site 1 (Upper Palumeu River), RAP Site 2 (Grensgebergte), and RAP Site 4 (Kasikasima). Ants were surveyed using hand search-collecting methods and the Winkler method (Agosti et al. 2000). In the search-collecting method, the ants nesting under stones, under or inside decayed wood and those foraging on ground, litter, tree trunk and plants were searched for and collected. This method was employed at all three camps around the camp and in the forest along the principal trails. The second sifting method used was the Ants of the Leaf Litter (ALL) protocol (Agosti et al. 2000). Along each transect, a 1×1-m quadrat was set up every 10 m (for a total of 10 quadrats per transect). The leaf-litter, rotten twigs, and first layer of soil present in the quadrat were collected into a cloth sifter and shaken for about a minute. Within the sifter was a wire sieve of 1-cm² mesh size, which allowed small debris and invertebrates such as ants to fall through the mesh into the bottom of the sifting sack. The sifted leaf litter was then placed in a full-sized Winkler sack, which is a cotton bag into which four small mesh bags containing the leaf litter are placed. Due to their high level of activity, ants run out of the litter and the mesh bag and fall to the bottom of the sack into a collecting cup of 95% ethanol. The Winkler sacks were hung in the field lab for 48 hours. A total of 10 Winkler Transects were sampled at the following sites: • Upper Palumeu (RAP Site 1, approx. 270 m a.s.l.): Two 100 m winkler transects were sampled in the forest along the trail to Brazil, starting after the helipad. Leaf litter was dry and fairly thin. Two 100 m winkler transects were sampled in the forest up the hill behind the camp. 5 days collecting. • Grensgebergte (RAP Site 2, approx. 800 m a.s.l.): One 100 m winkler transect was sampled in forest behind the RAP tent. Leaf litter was very wet due to heavy rain the night before and in the morning. One 100 m winkler transect was sampled in the forest at the top of the mountain above the rocky outcrops. Litter was wet and thick. These two transects were combined when hung in the Winkler sacs due to logistical difficulties when RAP Camp 1 flooded. 1 day collecting. • Kasikasima (RAP Site 4, approx. 200 m a.s.l.): Two 100 m winkler transects were sampled along the trail by the river (towards the METS camp). Three 100 m winkler transects were sampled in forest along the trail between the RAP camp and the Kasikasima rock, most on the tops of hills on flat plateaus. 6 days collecting. The ant specimens were preserved in 95% ethanol and sorted to morphospecies. Some specimens were identified to species level by L. Alonso and J. Sosa-Calvo using ant taxonomic literature and the ant collection at the National Museum of Natural History in Washington, D.C. PRELIMINARY RESULTS For this report, ants from six of the 10 winkler transects were sorted and identified to morphospecies. These included: 2 transects from RAP Site 1 (Upper Palumeu), 2 transects from RAP Site 2 (Grensgebergte), and 3 transects from RAP Site 4 (Kasikasima). Only a few of the hand collecting samples have been identified so far, with an emphasis on the ants collected from ant-plants. A total of 149 ant morphospecies representing 35 genera and 10 subfamilies were identified from the sorted collections (see Appendix 7.1). Most of the species were from the Winkler transects since only a few of the hand collections have been sorted so far. Additional work is ongoing to process and identify the remaining samples, which will undoubtedly raise the total number of species, possibly to over 200 species. A total of 72 ant species were recorded from RAP Site 1, 25 species from RAP Site 2, and 92 species from RAP Site 4 (Appendix 7.1). Genera typical of the region including many large ants that were commonly seen in the forest, including the arboreal species Daceton armigerum, Cephalotes spp., and Camponotus spp., the large-eyed terrestrial Gigantiops destructor, and several species of army ants. Many species of tiny leaf litter dwelling dacetines (Strumigenys, Octostrumd) were collected at all three sites, indicating good primary forest. Species of the genera Pheidole, Pachycondyla and Odontomachus were commonly observed and collected. Pheidole was the most speciose genus, which is typical for tropical rainforest. Many ant-plants in the family Melastomataceae (Tococa sp.?) were found in the area, housing obligate ant mutualists in domatia at the base of leaves. Most of these plants contained Pheidole (possibly cf. minutula) or Crematogaster sp. 7. The ant-plant Hirtella duckei (Chrysobalanaceae) was collected at RAP Site 4 and housed Allomerus sp. (see page 26) Pseudomyrmex sp. was collected from Triplaris near the Kasikasima Camp (Site 4), and Azteca sp. was collected from Cecropia on top of the rock at RAP Site 2. One or two species of fire ants, Solenopsis spp., were collected during the RAP survey. They may both be S. geminata, the tropical fire ant, which is native to the region. A light orange species was found under a log in the forest near RAP Camp 1 and in Palumeu village, and a darker species was common on open rocks on top of the Grensgebergte mountain (Site 2) at about 500 m. Further study is needed to determine the species. DISCUSSION Ants were abundant at the Southeastern Suriname RAP sites but did not seem as numerous or conspicuous as they were at the Werehpai RAP site during the Kwamalasamutu RAP survey (Alonso 2011). Much of the area surveyed was in seasonally flooded forest, which may partially explain the perceived lower abundance of ants and thin leaf litter in many areas. The forest between the RAP camp at RAP Site 1 (Upper Palumeu River) and the helipad became completely inundated on August 17. Ants and other organisms in the leaf litter are adapted to this environment and often must move when the floodwaters come. Atta sp. (leaf cutting ants) nests were observed only on higher terra firme ground. Tropical lowland rainforests typically harbor a high diversity of ants. For example, Longino et al. (2002) found over 450 ant species in an area of approximately 1500 ha in Costa Rica, and LaPolla et al. (2007) reported 230 species from eight sites in Guyana. A RAP survey in Papua New Guinea (Lucky et al. 2011) reported 177 ant species from the low-land site (500 m). More studies of ant diversity throughout Suriname are needed to estimate the country's ant diversity, and thereby provide important baseline data for conservation and management of Suriname's biodiversity. While in-depth analysis cannot be done until all the ant samples have been processed, these preliminary results indicate that Southeastern Suriname has high ant diversity. Data from winkler transects sampled at eight sites in Guyana (LaPolla et al. 2007) reveal comparable levels of ant species richness per transect. The winkler transects done in Guyana included 20 samples each while those from this RAP survey included 10 samples each. Thus two transects from this survey would roughly equal the sampling effort of one transect in Guyana. Table 7.1 shows the number of ant species recorded in each of the Winkler transects in this RAP survey and in Guyana at comparable elevations. Table 7.1. Number of ant species recorded in per Winkler transects during this RAP survey of Southeastern Suriname (this RAP survey) and from Guyana (LaPolla et al. 2007). Likewise, further analyses are needed to determine if there are differences between the ant species composition of the three RAP sites sampled in Southeastern Suriname, and also between Southeastern Suriname and other sites within the Guiana Shield. However, the preliminary morphospecies data for the six winkler transects sorted suggest that there may be some differences in species composition between the sites (see Appendix 7.1). Many of the leaf litter ant morphospecies identified so far (collected in Winkler transects) were found at only one of the RAP sampling sites. RAP Sites 1 and 3 were sampled for an equivalent amount of time (5 and 6 days respectively) so further comparisons can be made between the two sites. Altitudinal differences in ant species richness and composition have been well documented in many tropical regions of the world with higher richness at lower elevations (Johnson and Ward 2002, Lessard et al. 2007). Thus it may be that the Grensgebergte site (RAP Site 2, 800 m) has lower ant richness than the two other sites. However, this difference is more likely due to the almost constant rainy conditions during sampling at that site and to the short duration of sampling there (1 day). The site was overcast with clouds during most of the survey. The winkler transect was collected during rain and thus the leaf litter was very wet and sticky. Furthermore, the leaf litter sample had to be taken to RAP Site 1 to be hung in the winkler sacks, but RAP Camp 1 flooded at that time and thus the sample was hung two days later, which likely affected the survival of the ants in the sample. Ants play many critical roles in the functioning of the tropical terrestrial ecosystem, including dispersing seeds, tending mutualistic Homoptera, defending plants, preying on other invertebrates and small vertebrates, and modifying the soil by adding nutrients and aeration (Philpott et al. 2010). Another critical function provided by ants is that of scavenging (see page 27); ants are often the first animals to arrive upon a dead animal and start the decomposition process. Ants are particularly important to plants since they move soil along the soil profile through the formation of their mounds and tunnels, which directly and indirectly affects the energy flow, habitats, and resources for other organisms (Folgarait 1998). Thus ants are important to study and to include in conservation planning. ANT SPECIES OF NOTE Several ant species in Southeastern Suriname are common and conspicuous and have interesting life histories and behaviors. These ant species can thus serve to highlight the key roles that ants play in the ecosystem. Gigantiops destructor —the Jumping Ant—is a large black ant common on the forest floor in the Werehpai area. These ants have extremely large eyes with which to see and avoid their predators and their prey. They move very quickly and actually jump around on the leaf litter, which is unusual for an ant. Despite its name—destructor—these ants are timid, so you have to sneak up on them carefully. They do not bite or sting but defend themselves by spraying formic acid from their gaster. These ants forage for small invertebrates in the leaf litter and are often found nesting near Paraponera clavata nests, possibly to benefit from the aggressive defense of the larger ants. Daceton armigerum —the Canopy Ant—is a beautiful golden-colored ant that lives high in the canopy of trees. They have large heads with strong muscles that power their sharp mandibles. Their eyes are under their head so that they can see below them as they walk along branches in the tree-tops. Another key to their success in the canopy is that their claws are very clingy and can keep a tight hold on branches and tree trunks. Cephalotes atratus —the Turtle Ant, or Gliding Ant, lives high up in the tree canopy. With its flattened body and large turtle-shaped head, it lives within rotting twigs and branches and blocks the entrance to its nest with its head. Living so high in the canopy, these ants face the threat of falling out of their tree into the terrestrial territories of other, more ferocious ants. Thus they have evolved a way to avoid falling to the forest floor. If they fall from their tree, these ants stretch out their bodies and legs to glide (Yanoviak 2005). They can detect the tree trunk by the relative brightness against the dark greenery and twist in the air to point their abdomen toward their host tree, making a safe landing back home. Eciton burchellii —the Army Ant—has very large colonies with millions of workers that move through the forest in a swarm raid, capturing everything in their path. These ants do not have a permanent nest but have a “bivouac”—a temporary nest site consisting of a giant ball of ants, usually found under a rotting log or in the hollow of a tree. These ants sting and bite and are very aggressive, even to humans, so one needs to watch where they step around these ants. It is very interesting to watch an army ant swarm since many other creatures can be seen jumping and running to get out of the path of the ants, and some specialized antbirds follow the swarm to catch these invertebrates for their meal. The soldiers of E. burchellii have very long mandibles that are used to suture wounds by some indigenous peoples. In addition to their swarms for catching food, these ants are also often seen moving their colony to a new bivouac (which is necessary when they run out of food in an area), carrying their larvae and pupae slung under their bodies. Odontomachus spp.—Trap-Jaw Ants—are large ants common on the forest floor (see page 27). These ants hold the world record for the fastest reflex in the animal kingdom. They forage by walking around with their mandibles (jaws) wide open. They have small trigger hairs between the mandibles that detect prey items (such as small invertebrates) and trigger the mandibles to snap shut very quickly to capture the prey. These ants often nest in the leaf litter trapped in small palm trees, in the terrestrial leaf litter, or in the soil. They are long, sleek, elegant ants, but have a nasty sting, so care must be taken to avoid touching them. Paraponera clavata —the Bullet Ant or Congo Ant—is famous for its very powerful and painful sting. It is one of the world's largest ant species and is common in Neotropical lowland rainforests. These ants nest in the ground at the base of trees but forage up in the tree-tops on nectar and invertebrates. While they forage solitarily, they often have a relay of ants for passing large nectar droplets from the treetops to the nest, from one ant to another. These ants are one of the few ant species that make sound to communicate with one another. They can “stridulate” by rubbing their legs along their thorax to make a high-pitched squeaky sound. Atta sp.—the Leaf-cutting Ant—is well known for its unique and fascinating agricultural lifestyle. Atta are fungus-growers—the workers cut pieces of leaves from a wide variety of trees to bring back to their nest where the leaves are chewed up by smaller workers and inserted into a large fungus garden, which the ants tend and cultivate. The ants do not feed on the leaves. Instead, they feed the fruiting bodies of the fungus to their larvae. Their nests are very large with many large underground chambers. It is fun to watch the workers cutting leaves and carrying them over their head back to the colony. Atta are parasitized by tiny phorid flies, which lay their eggs on the ants. When a fly larvae hatches, it burrows into an ant's head and develops inside, thereby killing the ant. Small Atta workers are often seen hitching a ride on the leaf carried by a larger worker- it is thought that these small ants serve to ward off attacking phorid flies. Pseudomyrmex spp.—the Tree-dwelling Ants. Many species live in the rotting, hollow twigs and branches up in the trees. They often fall from the trees, landing on the top of tents and even on your shirt, especially after a wind blows through the forest. Some species are specialized, obligate inhabitants of ant-plants, which provide a hollow cavity and sometimes food bodies or nectar for the ants. In exchange, the ants protect the plant by capturing and eating herbivorous insects that may eat the plant. These ants have large eyes and very long, slender bodies (their body form is distinctive) and a painful sting, so it's best to take care when observing them. CONSERVATION DISCUSSION AND RECOMMENDATIONS The ant data from this RAP survey are part of an ongoing program of the “Ants of the Guiana Shield” led by Dr. Ted Schultz of the Smithsonian's National Museum of Natural History in Washington, D.C. and collaborators. These data will be combined with the winkler data collected by J. LaPolla and colleagues in Guyana (LaPolla et al. 2007), data from previous RAP surveys, and future surveys in the Guiana Shield to determine hotspots of ant diversity and endemism in the Guiana Shield to guide conservation priorities. The data will also be used to select indicator groups that can be used to more quickly assess the status of the ant community and the ecosystem. Data on ants and other invertebrates are important since these groups may be able to illustrate differences between habitats within the Guiana Shield that larger animals with wide geographical ranges do not discern. This will aid in identifying important areas of the Guiana Shield for conservation. More data should be collected on ants and other invertebrates for the Guiana Shield in order to determine these patterns. Like many tropical taxa, many ant species and populations face a range of threats. The most immediate and widespread threat comes from the loss, disturbance, or alteration of habitat. Fragmentation studies have revealed that ant species richness and genetic diversity can be affected even in large forest patches of 40 km² (Brühl et al. 2003, Bickel et al. 2006). Nomadic ant species such as army ants need large expanses of habitat to find enough food to feed their exceptionally large colonies (Gotwald 1995). Likewise, deforestation and forest fragmentation can cause local extinctions of the neotropical swarm-raiding army ant Eciton burchellii and other army ants (Boswell et al. 1998, Kumar and O'Donnell 2009). Global climate change is likely already affecting the distribution of many ant species. For example, Colwell et al. (2008) predict that as many as 80% of the ant species of a lowland rainforest could decline or disappear from the lowlands due to upslope range shifts and lowland extinctions (biotic attrition) resulting from the increased temperature of climate change. Solenopsis geminata is native to South American rainforests but can become a destructive pest when it spreads into disturbed areas or is introduced to other parts of the world. This species was present in disturbed areas in the villages and could become more widespread in the forest if it moves in along trails. This species often invades areas that have been disturbed so their absence is a good sign of a healthy ant fauna and ecosystem. It is recommended to survey and monitor the presence of this species on the trail to Kasikasima to avoid spread of this species by humans. Given that ants are highly conspicuous and abundant in Southeastern Suriname they should be a key component of nature walks and eco-tourism visits in the region. Several ant species are large enough to attract the attention and admiration of tourists. These ant species have fascinating life histories and behaviors that give them “personalities” which tourists will find fascinating. Many ant species require closed canopy forest to maintain the appropriate microclimate they need to survive. These species are found only at pristine sites. Preliminary indications of the ant fauna at all three sites indicate the presence of many forest species among the ant fauna. A full analysis of the ant species, once identified, will reveal whether any ant species are of conservation concern and also how some of the ant species can serve as indicators of the health of the ecosystem. Southeastern Suriname is one of the last extensive pristine rainforests of the world, containing high and unique biodiversity. This region should be protected from fragmentation by development such as roads and hydropower projects. Likewise, mining and other extractive industries should also be prohibited in the region to avoid impacts on the forests, its species, and the freshwater resources of the region. REFERENCES 1 AgostiD. J.D.Majer L.E.Alonso T. R.Schultz 2000Ants: Standard Methods for Measuring and Monitoring Biological Diversity.Smithsonian Institution PressWashington, D.C. USAGoogle Scholar 2 AlonsoL. E.2000Ants as indicators of diversity In Ants, Standard Methods for Measuring and Monitoring Biodiversity D.Agosti J.Majer L. E.Alonso T. R.Schultz Washington, DCSmithsonian Institution PressGoogle Scholar 3 AlonsoLE. 2011A preliminary survey of the ants of the Kwamalasamutu region, SW Suriname In B.O'Shea L.E.Alonso T.H.Larsen A rapid biological assessment of the Kwamalasamutu region, Southwestern Suriname.RAP Bulletin of Biological Assessment 63. Conservation InternationalArlington, VA, USAAntWeb. Accessed June 19, 2013. www.antweb.orgGoogle Scholar 4 5 6 7 8 9 GotwaldW. 1995Army Ants: The Biology of Social Predation.Cornell University PressIthaca, NY, USAGoogle Scholar 10 11 KaspariM. J.D.Majer 2000Using ants to monitor environmental change. In Ants, Standard Methods for Measuring and Monitoring Biodiversity D.Agosti J.Majer L. E.Alonso T. R.Schultz Washington, DCSmithsonian Institution PressUSAGoogle Scholar 12 13 14 15 16 LuckyA. E.Sarnat L.E.Alonso 2011Ants of the Muller Range, Papua New Guinea. In RichardsS.J. GamuiB.G. Rapid Biological Assessments of the Nakanai Mountains and the upper Strickland Basin: surveying the biodiversity of Papua New Guinea's sublime karst environments. RAP Bulletin of Biological Assessment 60.Conservation InternationalArlington, VAGoogle Scholar 17 PhilpottS.M. IPerfecto I.Armbrecht C.L.Parr 2010Ant diversity and function in disturbed and changing habitats. In L.LachC.L.ParrK.L.DDabbottAnt Ecology, Oxford University PressNew York, USAGoogle Scholar 18 Sosa CalvoJ. 2007Ants of the leaf litter of two plateaus in Eastern Suriname. In AlonsoL.E. J.H.Mol A Rapid Biological Assessment of the Lely and Nassau Plateaus, Suriname (with additional information on the Brownsberg Plateau). RAP Bulletin of Biological Assessment 43. Conservation InternationalArlington, VA, USAGoogle Scholar 19 Appendices Appendix 7.1. Ants collected during the 2012 RAP survey of Southeastern Suriname. W=winker leaf litter transect, H=hand collecting continued continued continued
... The Allophrynidae is among the most enigmatic groups of frogs in the world. This family currently consists of just three species, two of which were described within the last 12 years (Gaige 1926;Castroviejo-Fisher et al. 2012;Caramaschi et al. 2013). Very little is known about these groups' reproductive biology. ...
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Frogs of the Allophrynidae are an enigmatic family from South America. To date, published information is lacking regarding this group’s reproductive biology and larval morphology. Here, we provide the first detailed description of the reproductive mode, developmental mode, and tadpole morphology for Allophryne ruthveni. We developed a captive breeding and rearing protocol for this species and then conducted a series of observations to describe aspects of its reproductive biology. In captivity, this species exhibits aquatic oviposition, where single eggs are laid ungrouped within a simple jelly capsule and are scattered free in the water column before sinking to develop on benthic substrates. We did not observe parental care nor any parental interactions with eggs post-fertilization. Tadpoles are characterized by an oval body, anteroventral oral disc, a labial tooth row formula of 2(2)/3, and a dextral vent tube. The buccopharyngeal cavity is marked by the presence of two pairs of infralabial papilla and four lingual papillae. Cranial morphology is characterized by the presence of the commissura quadratoorbital. This species possesses an additional slip of the m. rectus cervicis and of the m. levator arcuum branchialium III. We discuss our results in comparison with glassfrogs (Centrolenidae). Supplementary Information The online version contains supplementary material available at 10.1007/s00114-024-01910-y.
... Allophrynidae: This family contains a single genus, Allophryne, and until this year was monotypic (Castroviejo-Fisher et al. 2012). The species we encountered, A. ruthveni is distributed throughout the Guiana Shield (GS; LaMarca et al. 2010). ...
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We conducted a herpetofaunal inventory at four sites in Southeastern Suriname from March 8–28th 2012, and recorded 47 species of amphibians and 42 species of reptiles. These numbers are lower than other areas within the Guiana Shield that are better sampled (e.g. Iwokrama, Guyana; Nouragues, French Guiana), but are relatively high when compared with other sites sampled over the same time period (e.g., recent RAP surveys in Suriname). Seven (six frogs and one snake) of the total 89 species encountered could not be assigned to any nominal species. These unidentified taxa may represent novel species, yet require validating genetic and morphological data before formal diagnoses can be made. A number of records represent range expansions for taxa within the Guiana Shield (e.g. Rhinatrema bivitattum, Alopoglossus buckleyi). Additionally, a teiid lizard (Cercosaura argulus) is recorded for just the second time in Suriname. Encountering >80 total species (including 19 snake species) is evidence of a healthy, diverse and seemingly pristine forest ecosystem. INTRODUCTION Reptiles and amphibians form a prominent, speciose component of tropical forests and many aspects of their biology (e.g. small body size in concert with large population sizes, intermediate roles in food webs, strict micro-habitat requirements, etc.) contribute to their value as a focal group for biotic surveys. Amphibians are very good indicators of disturbance (Stuart et al. 2004) because they are sensitive to changes in microclimate, particularly as most possess a biphasic lifestyle (i.e. two distinct life stages, larval and adult) heavily dependent on high quality water resources. Amphibians are well suited for rapid assessments as they are often easy to sample; but when that is not the case, their species-specific diagnostic calls aid passive identification, particularly for hard to collect species (e.g. canopy dwellers; Marty and Gaucher 2000). Biotic surveys of amphibians in particular are imperative as widespread and poorly understood disease vectors (e.g. chytrid fungus and ranavirus) are causing worldwide declines, even in seemingly pristine areas (Lips 1998). Lizards are more diverse in primary forest, compared to secondary or modified forest (i.e. plantation; Gardner et al. 2007), suggesting they are also sensitive to changes in micro habitat. Presence of turtles and tortoises can also be a good indicator of hunting pressure as they are often targeted for subsistence hunting by local Amerindians (Peres 2001). Although one of the smallest South American countries, Suriname possesses a wide variety of amphibians (>100 species according to Señaris and MacCullough 2005; 107 species according to Ouboter and Jairam 2012) and reptiles (>170 species; Ávila Pires 2005). While very few of these species are endemic to Suriname itself, most are endemic to the larger Guiana Shield or the more inclusive Amazo-Guianan Subregion. The goal of this RAP survey in southern Suriname was to provide baseline information on the diversity and abundance of amphibians and reptiles for the areas in and around the Grensgebergte and Kasikasima Mountains. We sampled four sites incorporating both upland and lowland habitat, from seasonally flooded forest to human modified secondary forest to exposed granite outcrops. We also provide basic statistics comparing our findings with other RAP surveys in Suriname, as well as other well-studied regions in the Guianas (e.g. Iwokrama, Guyana; Nouragues, French Guiana). Finally, we discuss conservation recommendations for the region. METHODS Of the four main RAP study sites, herpetological collections were made in only three (Upper Palumeu River — Site 1 [9 days], Grensgebergte Mountains — Site 2 [2 days], and Kasikasima — Site 4 [6 days]; the unsampled site (Site 3) was visited only by the aquatic team while they were heading downriver between Sites 1 to 4). In addition, some species were encountered at the METS resort in Palumeu (Site 5 [1 day]), a subset of which was encountered at other sites. In order to encounter as many species as possible, opportunistic encounters and captures were made primarily via active searching. We walked pre-established trails through forest, in forest clearings, and on stream banks. Surveys were conducted at various times of the day (although focusing on main activity periods at dusk and dawn) and early evening to mid-night. Passive frog call surveys were performed at night and if the calling male was suspected of being near the ground, efforts were made to locate it. Special attention was taken to search in a variety of habitats, particularly in streams/creeks and under logs/fallen bark — areas known to harbor rarely seen species or those with strict habitat requirements, as well as after inclement weather (i.e. heavy rains). We turned stones and logs, opened rotting logs, and raked litter to reveal hidden animals. At times, we deviated off of the main trail/transect to search adjacent habitat or features (e.g. fallen log, swampy pool) we deemed of interest or where animal activity was observed. Opportunistic surveys are effective for collecting as many species as possible in a short time period and sampling total species richness (Donnelly et al. 2004). Unfortunately, care was not taken to painstakingly record each individual of each species encountered, so only qualitative assessments of species relative abundance are provided (Appendix 9.1). When possible and/or necessary, animals were caught either by hand, noose, net or rubber band, and preliminary identifications were made. Additionally, a portion of the total catch was euthanized (via subcutaneous injection of dilute Euthanaze®), fixed in 10% formalin solution, and then stored in 70% ethanol as museum voucher specimens (stored at the National Zoological Collection of Suriname, Anton de Kom, Universiteit van Suriname). These specimens were given unique field identification tags and many have representative life photographs (taken by S. Nielsen, P. Naskrecki and/or T. Larsen). R. Jairam later performed more rigorous, museum-based, morphological identification to verify species IDs. Samples of liver/muscle tissue for DNA analyses were extracted from voucher specimens (before formalin fixation) and stored in 95% ethanol (stored in the University of Mississippi frozen tissue collection). We compared data on amphibian and reptile surveys from five sites in the Guiana Shield (Nouragues and Arataye, French Guiana — Born and Gaucher 2001; Petit Saut, French Guiana — Duellman 1997; Piste Ste. Elie, French Guiana — Born and Gaucher 2001; and Iwokrama, Guyana — Donnelly et al. 2005) originally assembled by Watling and Ngadino (2007), as well as three additional sites from two previous RAP surveys in Suriname (RAP 43, Watling and Ngadino 2007; RAP 63, Ouboter et al. 2011). Although undetected and/or undescribed species certainly exist throughout the Guiana Shield, the non-RAP surveys — which occurred over multiple seasons — are better sampled compared to RAP surveys (which generally span just a number of days), therefore, direct comparisons must be viewed with some uncertainty. Additionally, the geological complexity of the Guiana Shield makes comparisons of species communities/composition between high elevation inselbergs and low elevation seasonally flooded forests difficult, as different habitats support different species and different overall levels of species richness may be expected may provide counterintuitive arguments. Instead, we provide these data as a benchmark with which to compare this current study. RESULTS AND DISCUSSION We observed a total of 89 species of reptiles and amphibians during this survey (Table 9.1). While most of the species are confidently sorted to known species, seven (six frogs and one snake) of the total species encountered could not be assigned to any nominal species and 23 are listed as cf., meaning only informal identifications are possible without more comparative material and rigorous morphological and/or molecular examination. Appendix 9.1 lists the species we recorded and a qualitative measure of abundance for each species for the four collection localities. Upper Palumeu River (Site 1) provided the most diverse list of species (56 species, 63% of total — 30 amphibians and 26 reptiles; of which, 12 amphibians and 16 reptiles were only encountered at Site 1; see Table 9.2). This result may partially be explained by the amount of time spent collecting in that locality versus the other sites (8 days total versus the 2nd longest stay — 6 days [Site 4]), thus affording us greater opportunity to encounter a wider variety of species. However, some other subtle vegetation or habitat differences might also have played a role (e.g. presence of seasonally flooded lowland forest in Site 1). Grensgebergte Mountain (Site 2: 13 species, 15% of total species encountered; 6 amphibians and 7 reptiles, of which 1 amphibian and 3 reptiles were only encountered at Site 2) was by no means speciose, but provided two unique snake records: Dipsas copei and the only sighting of Bothrops atrox. Kasikasima (Site 4) was the second most diverse site (45 species, 51% of total —24 amphibians and 21 reptiles; of which, 6 amphibians and 10 reptiles were encountered only at Site 4). Palumeu (Site 5) was not particularly diverse (18 species, 20% of total —13 amphibians and 5 reptiles; of which 7 amphibians and 2 reptiles were encountered only at Site 5), although we suspect that the surrounding area could potentially harbor other species. As the expedition was not focused on this area, the species encountered were all observed/collected within one 24-hr. period (including one rainy night) before continuing on to Site 1. Table 9.1. Herpetofaunal richness at 12 sites in the Guiana Shield, including data from the two previous RAP surveys to Nassau/Lely Mountains and Kwamalasamutu. In each column, data are presented as raw species number/percentage of total herpetofauna. Table 9.2. Breakdown of reptile and amphibian species encountered at each locality and the site-specific percentage of the total species recorded, as well as how unique each site was for both taxonomic groups. When the results for all localities are combined, our findings are comparable to those of RAP 63 of the Kwamalasamutu region of southwestern Suriname (Ouboter et al. 2011; see Table 9.1), which recorded 78 species of amphibians and reptiles (42 and 36, respectively), and is from a geographically close region. However, when each site is analyzed separately, our numbers are much more similar to those found by Watling and Ngadino (2007; RAP 43) in eastern Suriname, which also spent a similar amount of time sampling each of their two sites (-5 days). RAP 43 focused solely on areas of intermediate/high elevation, which harbored fewer (albeit more highland endemic) species. All recent RAP surveys, including the present study, generally recorded fewer species than other areas within the Guiana Shield (see Table 9.2), which can likely be explained by total days of search effort. A number of species (24 of 89 total sp.) were recorded at the two sites that received the greater proportion of our search effort (Sites 1 & 4). Of the species that were recorded at just one site (45 spp.), most had congeneric relatives present at other sites, possibly/effectively filling similar ecological niche space (e.g. the snake Atractus torquatus was present only at Site 1 and A. flammigerus only at Site 4; however, one could argue that these two species occupy similar niches in the ecosystem). Albeit an extraneous assumption, there remains the possibility that given more search effort, other congeneric (and potentially ecologically similar) species could also be found (or that competitive niche exclusion restricts them to microhabitats that we failed to survey adequately). This pattern is also seen when comparing our results to the two other recent RAP surveys (RAPs 43 & 63); of the 89 species recorded in the present study, RAP 43 (49 spp. total) recorded 23 (26%) and RAP 63 (78 spp. total) recorded 44 (49%) of the same species (see Appendix 9.1 and Table 9.1). However, in both of these two related surveys, congeneric species (which have the potential to be ecologically similar) were collected (see species marked as “N*” in Appendix 9.1). Thus, at a higher taxonomic scale, our results are similar (see further description below). A number of species that were recorded by these previous RAPs were noticeably absent from our collection efforts (e.g. frogs such as the microhylid, Chiasmocleis shudikarensis, the ceratophryid, Ceratophrys cornuta, and the pipid, Pipa aspera), although these species are generally less likely to be sampled due to their cryptic, semi-fossorial, and/or fully aquatic lifestyles. The ∼104 currently recognized amphibian species recognized in Suriname are representative of 38 genera in 13 families (Señaris and MacCullough 2005, Ouboter and Jairam 2012). Due to the “rapid,” abbreviated nature of RAP surveys, we were unlikely to encounter all the biodiversity a geographic area harbors (especially as some of Surinames -104 amphibian species are restricted to coastal lowlands or other areas/habitat we were unlikely to survey in southern Suriname; see Ouboter and Jairam 2012). During the course of this RAP, we recorded -47 species from 19 genera and 7 families (45%, 50%, and 54% of Suriname's currently recognized totals, respectively). Considering the aforementioned shortcomings of this type of survey, capturing roughly 50% of the known amphibian biodiversity of Suriname is a positive result. By comparison, RAP 43 (36 spp. from 13 genera and 5 families) and RAP 63 (42 spp. from 19 genera and 10 families) each recorded approximately 35% and -50–70% of the diversity, respectively. Although we observed and/or collected a smaller percentage of the total reptile diversity of Suriname (-170 spp., 92 gen., 23 fam.), our results are roughly similar in pattern to those for amphibians outlined above. We collected 42 species from 37 genera and 17 families (25%, 40% and 74% of the Surinamese total, respectively). Similar to the above results, RAP 43 collected a smaller percentage of the total (17% of Suriname's total spp., 24% of gen., 48% of fam.), whereas RAP 63 had results similar to (albeit less than) the present study (21% of Suriname's total spp., 35% of gen., 65% of fam.). Why these results represent a larger proportion of the higher-level diversity than we recovered in amphibians is unknown, but could be representative of an underestimate of amphibian familial diversity. Without further work, it is difficult to say whether we adequately surveyed the region in our limited time during this survey, but we did achieve comparable results to recent, previous RAP surveys. Although the number of‘new’ or rare species we collected was comparatively low (and really awaits thorough taxonomic revision of a number of groups) the real value of this region was the great diversity of herpetofauna seen and/or collected in a short time. We propose that these results suggest that southern Suriname is a local hotspot for herpetofaunal richness and if conserved in this pristine/ semi-pristine state, this region will remain a true preserve of biodiversity. Below are brief accounts of some of the species/taxonomic groups we encountered that are of interest due to their conservation status, distribution, natural history or potential as a new species, etc. Class Amphibia, Order Anura Allophrynidae: This family contains a single genus, Allophryne, and until this year was monotypic (Castroviejo-Fisher et al. 2012). The species we encountered, A. ruthveni is distributed throughout the Guiana Shield (GS; LaMarca et al. 2010). Numerous individuals were ob served/captured at Site 1 that displayed a divergent color pattern when compared to “typical” A. ruthveni. As the recently described species from eastern Peru, A. resplendens, is diagnosed from A. ruthveni primarily on dorsal color pattern and mitochondrial DNA sequence divergence (Castroviejo-Fisher et al. 2012), we initially hoped we had found a third species for the genus. However, preliminary genetic data (unpub. 12S data) does not provide resounding evidence for elevating the Suriname population to a separate species. Further work is underway. Dendrobatidae: We encountered two subfamilies within this super group of dart-poison frogs, Dendrobatinae and Aromobatinae. The latter contains >100 species in five genera, whereas Dendrobatinae contains 12 genera and >170 species. These frogs are terrestrial, largely diurnal, and display a unique reproductive mode exhibiting parental care. Within Aromobatinae, we encountered four ‘species’ representative of two genera, Allobates and Anomaloglossus. Allobates femoralis is widely distributed across the Amazo-Guianan subregion (AGR; La Marca et al. 2010), whereas Allobates granti is distributed within a more limited area of the eastern GS (Kok 2008; Ouboter & Jairam 2012). Although neither species possessed particularly aberrant morphologies, Fouquet et al. (2012) has shown that there is considerable, geographically concordant genetic substructure across each species' respective range, potentially harboring complexes of cryptic species. As the taxonomie work is ongoing, it is difficult to accurately assess whether the populations sampled during this RAP survey are distinct from the larger Surinamese (or GS) groups delimited by Fouquet et al. (2012). Anomaloglossus baeobatrachus (IUCN Data Deficient) and Anomaloglossus sp. (see page 23) were abundant where they were found (Sites 1 and 4). Individuals of the latter found at the Kasikasima site possessed atypical (in comparison to A. baeobatrachus) dorsal color patterns (i.e. blotchy, not uniform). Similar to Allobates, Fouquet et al. (2012) has shown considerable, geographically concordant genetic divergence across these species' respective ranges, although it is currently unclear whether the Anomaloglossus “sp.” referenced in that paper is the same taxon we encountered on this RAP. Unfortunately, at present we have been unsuccessful at obtaining informative DNA sequence information to compare to that of Fouquet et al. (2012), although work is ongoing. Within Dendrobatinae, we encountered two species representative of two genera. Of the two species of Amereega that occur in Suriname, we found just A. trivitatta (see page 29), which is widespread across the AGR, although absent from the eastern GS. Such a wide distribution could harbor cryptic species, as has been found in closely related species within the genus (see Brown and Twomey 2009). However, of the individuals we collected, there was no significant morphological divergence to suggest that scenario. We encountered this species in three of our four collection localities (all lowland), including the relatively altered forest surrounding Palumeu (Site 5), where they were quite common. We also encountered Dendrobates tinctorius (see page 29), which is found only within the GS, but is unique in possessing highly variable, geographically isolated color patterns. Although there is some taxonomie contention whether the different morphs should be treated as unique taxa, genetic data suggests the different color morphs (i.e. populations) are representative of within species variation only (Noonan and Gaucher 2006). This taxon was only observed at Sites 1 and 2 (including egg masses and tadpoles at Site 1), although two strikingly different color morphs were found at each locality. At the Grensgebergte Mtns. Site (2), L. Alonso and P. Naskrecki encountered a differently colored morphotype of D. tinctorius compared to the lowland coloration found near Site 1, although based solely on a partially out of focus photo voucher we believe it to represent the “common” color morph. Bufonidae: This hyper-diverse, globally distributed family contains >35 genera with >500 described species, with a number of genera and species endemic to South America. Although only seven species were encountered on this RAP, they were by far the most abundant amphibians at each of the lowland sites (Sites 1, 4 and 5). The genus Amazophrynella was recently separated from Dendrophryniscus (Fouquet et al. 2012a), and of the two described and one undescribed species, one — A. minuta (see page 29) — has a broad AGR distribution that includes Suriname. Although the common name — tree toads — suggests an arboreal existence, we encountered numerous individuals at Sites 1 and 4 during the day hopping around in the leaf litter. Although we are fairly certain of their taxonomic placement based on morphology, evidence suggests this taxon is actually a species group (Coloma et al. 2010; Fouquet et al. 2012a). Further taxonomic work is required, albeit beyond the scope of this report. Rhaebo guttatus also has a widespread pan Amazo-Guianan distribution (Azevedo-Ramos et al. 2010). This prodigious species is terrestrial and nocturnal, and was common where it occurred (Sites 1 and 4). As it requires undisturbed primary forest, this species was absent from disturbed, human-modified areas (Site 5), where it was instead replaced by the more ecologically tolerant cane toad, Rhinella marina (e.g. observed around human habitation and in a maintained airstrip). Members of the genus Rhinella are generally nocturnal, explosive breeders, and representative species were found at all four sampled sites during this RAP survey. Rhinella marina has a large native distribution spanning from central South to southern North America, but is considered an invasive species in numerous other countries, notably Australia and the US (Solís et al. 2009). We also encountered at least three other species in this genus, R. lescurei, R. margaritifera and R. martyi. Rhinella lescurei and R. martyi are described species of the R. margaritifer species group (Fouquet et al. 2007), which is broadly distributed in primary rainforest across northern South America (Solís et al. 2009). We encountered a fourth form, R. sp., that we believe could be an additional member of the R. margaritifera group. Unfortunately, many of the specimens we collected were juveniles, and the named species are quite similar morphologically, so accurate identification has proven difficult. Further work is required. Centrolenidae: Members of this family are commonly called glass frogs, as their transparent venter makes visible their internal organs. They are nocturnal, colored in shades of neon green and are often found in overhanging vegetation along streams and rivers, although their coloration and behavior make them particularly difficult to locate. Suriname has at least five species of centrolenids (Ouboter and Jairam 2012). We collected just two specimens on this RAP survey, both tentatively identified as Hyalinobatrachium cf. taylori, which is widespread across the GS. Only one specimen was collected from each of the sites where they were present (Sites 1 and 4), although numerous males were heard calling at both places. Hylidae: This mega-diverse family is composed of “true tree frogs and their allies” comprising 900+ species in 45+ genera that are distributed mainly in the New World (particularly South and Central America) as well as Australia. They are nocturnal, generally arboreal and display a variety of reproductive modes. There are -40 species known from Suriname (Ouboter and Jairam 2012), however, just 15 were encountered on this RAP, representative of six genera. We collected six species of Hypsiboas treefrogs, including a putatively undescribed taxon, H. sp. “chocolate” (see page 23) and four species of Scinax, including a putatively undescribed taxon (see page 23) that we believe could represent a Surinamese population of a novel species proposed by Fouquet et al. (2007). The genus Scinax is in great need of revision and specimens we collected could represent novel species, but further evidence is required to better understand genetic patterns and species boundaries. These species were not particularly common, but representative hylids were present at each site — although not all species were present at each site. A single specimen of the species Trachycephalus coriaceus and two Dendropsophus cf. brevifrons specimens were recorded (one via cell phone camera photo). The former species has an interesting disjunct distribution with populations present in the eastern GS and southwestern Amazonia, but absent from northeastern Amazonia. Frogs from the genus Osteocephalus representing two species (O. taurinus and O. leprieuri) were some of the most commonly encountered vertebrates at Site 1, yet only a single individual of the latter was found at any of the other sites (Site 4). Lastly, we also recorded the charismatic tiger leg monkey frog species, Phyllomedusa tomopterna (see page 29) from Site 1. This species requires pristine forest habitat and is distributed widely across the AGR (La Marca et al. 2004). Leptodactylidae: Colloquially known as southern frogs, this group is composed of 190 species in 13 genera, all of which are restricted to the New World. This group of frogs is diverse in body size (e.g. 26mm SVL in Adenomera heyeri vs. 185mm in Leptodactylus pentadactylus) and in ecology (e.g. Lithodytes lineatus is often associated with ant nests, whereas Leptodactylus leptodactyloides prefers open areas like savannahs and forest edges). We found up to 12 different species (two currently identified to “sp.”) from three genera, -60% of Suriname's total leptodactylid diversity. Members of this family were observed at all four sites, with the greatest diversity of species from Sites 1 and 5 (i.e. Upper Palumeu and Palumeu). Most of the species we encountered are assignable to the genus Leptodactylus, although we also collected two forms we cannot yet accurately identify: Adenomera sp. and Leptodactylus sp.. With the exception of L. longirostris and L. myersi (which have a more restricted distribution in the GS), the species we encountered are all widely distributed across the AGR — and a few even extend into southern Central America. At site 2, L. myersi was the most abundant terrestrial vertebrate observed and it was quite easy to find juvenile frogs living in the moist spaces under nearly every granite exfoliation in the seeps on the exposed inselberg face. Craugastoridae: This family contains the most speciose genus of vertebrates, Pristimantis, with over 400 species (-5 in Suriname) of direct-developing frogs (i.e. lacks a living larval stage). Their deviation from the reproductive strategy norm, liberating them from semi-/permanent water sources, may be one reason for their widespread distribution and successful speciation in a variety of habitats. One described species was encountered (Pristimantis chiastonotus), which is distributed throughout the eastern GS. This species is found in leaf litter, generally at low altitudes (<700m asl), and it has been suggested that they are able to cope with some degree of habitat disturbance (Gaucher and Rodrigues 2004). We also collected individuals not immediately identifiable to a named species (which we are calling Pristimantis sp.) (see page 23). We found Pristimantis species at all four collection localities, including disturbed habitat (i.e. Palumeu) and in the Grensgebergte Mtns. (roughly 750m asl). Class Amphibia, Order Gymnophiona Rhinatrematidae: This family of caecilians (a fossorial group of primitive, limbless amphibians) is composed of two species-poor genera endemic to South America. Only one species was encountered on the RAP, Rhinatrema bivitattum (see page 28), which appears to be distributed across the northern Guiana Shield, from Guyana to Brazil (Gaucher et al. 2004). It was previously only known from the Brownsberg region of Suriname (Nussbaum and Hoogmoed 1979) and thus our record represents a significant southern range extension. Our local guides collected a single specimen while clearing the area of vegetation for the tent camp at Site 1. Class Reptilia, Order Squamata Gekkota: This diverse lizard group has a near worldwide distribution as geckos are found on every continent but Antarctica. Representatives of three families (Sphaerodactylidae, Phyllodactylidae and Gekkonidae) were encountered during this RAP survey. All three families have representative species from the New and Old Worlds, as well as northern and southern hemispheres, although the history of occupation in the New World for sphaerodactylids and phyllodactylids is much older than for gekkonids. Gamble et al. (2011) found evidence to suggest that modern New World sphaerodactylids reached northern South America in the Cretaceous before the break-up of Gondwana (i.e. Gondwanan vicariance), and phyllodactylids arrived shortly thereafter (either via vicariance or dispersal), whereas geckos in the family Gekkonidae reached the New World much later (i.e. within the last 5–10 mil. yrs.) via long-distance, over-water dispersal. We only encountered one species of gekkonid on this RAP, Hemidactylus mabouia, which is native to Africa, although it can now be found throughout South and Central America and the Caribbean (via either natural or anthropogenic forces of dispersal). This species was common on the main building of the METS resort in Palumeu. The sphaerodactylid gecko species, Gonatodes humeralis, was also fairly common in primary forest and forest edges (Sites 1, 4 and 5) and is distributed widely across northern South America. Although neither was common, the two other sphaerodactylids encountered, G. annularis (see page 28) and the rather diminutive Pseudogonatodes guianensis, are restricted to moist microhabitats generally in lowland forest (although the former can be found at -800m on the Tafelberg; Ouboter pers. comm.). We consider encountering both of these species as a good indicator of forest health. Lastly, we encountered the phyllodactylid gecko Thecadactylus rapicauda, a prodigious species that reaches 125mm in snout-vent length. What was once considered one widely distributed taxon found throughout northern South America, Central America and the Lesser Antilles, this species has recently been split into three (T. solimoensis is restricted to the western Amazon and T. oskrobapreinorum from Sint Maarten). This species is sometimes commensal with man-made structures. Lacertiformes: This morphologically and ecologically diverse group (sensu Townsend et al. 2004) is distributed throughout the Americas and includes three lizard families: Teiidae, Gymnothalmidae and Amphisbaenidae. Teiid and gymnothalmid lizards were the most commonly encountered reptiles at each site during this RAP. Species of lizards in these families are active hunters and were commonly encountered moving through the leaf litter (e.g. Alopoglossus, Arthrosaura, Leposoma), in streams/pools (e.g. Neusticurus) (see page 28), under logs (e.g. Gymnopthalmus), or moving in the open near tree falls and around camp (e.g. Ameiva, Kentropyx). The existence of Cercosaura argulus in Suriname was previously based on one record from Palumeu (Hoogmoed 1973) and the distribution map provided by the IUCN website does not confirm its presence in the country (Doan and Avila-Pires 2010). We here provide confirmation of its residence in southern Suriname. Additionally, our tentative taxonomic designation for Alopoglossus buckleyi would suggest a significant range extension for this taxon. There are morphological differences separating this taxon from the widespread A. angulatus (corroborative genetic data is also being gathered), however, this designation is still tentative and will require more comparative material for us to be confident. A single worm lizard putatively identified as Amphisbaena cf. vanzolinii (see page 28) was encountered during the second night at Site 4 moving through our recently constructed camp. This taxon — like most amphisbaenian species — is infrequently collected due to its fossorial habits but it appears to be patchily distributed across the western AGR. Scincomorphs: Skinks are the second most diverse squamate group (behind Gekkota) and are also distributed nearly worldwide, although there are only -18 species in South America. We encountered a single species, Mabuya nigropunctata, at all forest sites — including high elevation — and were commonly observed basking or foraging around open canopy tree falls. Mabuya nigropunctata is widespread across Amazonia and can even be found in St. Vincent in the southern Caribbean. Miralies and Carranza (2010) recently published molecular evidence suggesting this taxon might be a complex of three largely allopatric lineages, although they did not suggest new names for the distinct lineages they recovered. We observed numerous individuals at Sites 1, 2 and 4, yet this wily taxon successfully evaded capture so we have no voucher or genetic material with which to compare to Miralles and Carranza (2010). Serpentes: According to Ávila Pires (2005), Suriname possesses more than 100 snake species from 8 families. Although most of our records were of single individuals, we encountered 19 species from 6 different families. While this may seem like a paltry sum compared to the total, snakes in general are difficult to collect due to their cryptic biology, and some are restricted to specific habitat types/food sources (e.g. mangroves) that were not targeted or near the sampling sites of this study. By comparison, the two previous RAP surveys to Suriname, Lely/Nassau (RAP 43) and Kwamalasamutu (RAP 63) recorded just 6 and 17 snake species, respectively. The family Colubridae comprised the majority of the species we encountered (13 sp.), including the most commonly encountered species (i.e. the Blunthead Tree Snake (Imantodes cenchoa) and two species of ground snake (Atractus spp.), although still only a small fraction of Suriname's total colubrid diversity (>75 sp.). Colubridae is the largest snake family and includes about two-thirds of all described snake species (>300 genera, >1,900 species). Site 2 (Grensgebergte) provided the only records of Cope's Snail-eater, Dipsas copei, and the fer-de-lance, Bothrops atrox. There is some confusion regarding the type locality of the former (i.e. Suriname; see Kornacker 1999), although undoubtedly it is quite rare and is represented by only a handful of specimens collected in Suriname. The fer-de-lance on the other hand is often one of the more common snakes encountered in lowland tropical forests; yet we saw only one, and at >700 m. We posit that this is a result of undersampling rather than absence of the species from the lowland sites and if we had utilized pitfall trap arrays with funnel traps on this survey, we are confident we would have encountered more “common” terrestrial species, such as Bothrops spp. Testudines: Although only a few individuals of two species were observed, we argue that presence of turtles and tortoises are positive signs of limited hunting pressure. Due to their ease of capture and convenient storage, humans have been subsistence hunting tortoises for millennia (Thorbjarnarson et al. 2000) and many cultures in South America continue this practice. A single individual of the flat-headed turtle, Platemys platycephala, was observed by R. Jairam at Site 1 foraging in partially flooded lowland forest. At least two different individuals of the yellow-footed tortoise, Chelonoidis denticulata, were encountered at the high elevation site 2, sitting in vegetation near slowly flowing seeps, while a third individual was also observed foraging in the lowlands between camp and Kasikasima mountain (Site 4). While by no means an extensive survey, the presence of these species is likely correlated to the seemingly pristine quality of the forests. CONSERVATION RECOMMENDATIONS Of the species we encountered, only a fraction has been assessed for the IUCN Red List of Threatened Species, and most are listed as Least Concern or Not Evaluated since they are widely distributed across either the greater Guiana Shield or some portion of Amazonia. Due to myriad factors (e.g. weather, collection technique, collector fatigue), it is likely that we failed to collect all representatives of the herpetofaunal community at each site. With repeated surveys, we expect that our species lists would increase. Given the amount of time available at each site, we found a community that appeared speciose and could be harboring a few putatively “new” species (e.g. Hypsiboas sp. “chocolate”). This survey also provided collection records that have contributed to geographic range extensions for species not previously known from Suriname (e.g. Cercosaura argulus and Alopoglossus buckleyi), as well as new records for particularly rarely encountered species (e.g. Dipsas copei, Rhinatrema bivittatum, Amphisbaena cf. vanzolinii). Observing little in the way of disturbance or man-made alterations, we suggest that these sites (with the possible exception of the altered forest near Palumeu) are healthy and productive, and are presumably acting as a corridor for gene flow through this region of the Guiana Shield. The presence of species that are rarely seen or were previously unrecorded in Suriname helps to substantiate that there is (or was) an historical connection between this and surrounding areas. 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F.Ngadino 2007A preliminary survey of amphibians and reptiles on the Nassau and Lely plateaus Eastern Suriname. In: AlonsoL.E. J.H.Mol A rapid biological assessment of the Lely and Nassau plateaus, Suriname (with additional information on the Brownsberg Plateau). RAP Bulletin of Biological Assessment 43.Conservation InternationalArlington, VA, USA119125Google Scholar Appendices Appendix 9.1. Amphibians and reptiles recorded during the current RAP study. A qualitative assessment of species abundance for each site where the occurred is included (VC: very common, >10 individuals observed; C: common, l>x >10 individuals observed; UC: uncommon, only 1 observed/captured), as well as general geographic distribution (W: widespread; GS: Guiana Shield; AGR: Amazo-Guianan Subregion; E: exotic), IUCN threat status (LC: least concern; NE: not evaluated; DD: data deficient) and type of microhabitat in which the species was recorded. The last two columns indicate whether the same (Y or N) species were recorded by the two most recent RAP surveys in Suriname. In some cases, congeners (N* i.e. a close taxonomic relative) were recorded instead of the species we documented in the present study. Continued Continued Continued Continued
... Amphibians generally have a low vagility and high philopatry, which are characteristics that promote differentiation and ultimately speciation (Wells 2012. In this sense, although most anuran species would be expected to have small geographic distributions with distantly separated populations having greater genetic differences, there are some cases of widely distributed species with low genetic distances, such as Dendropsophus nanus (Boulenger, 1889) (Fouquet et al. 2007), Allophryne ruthveni Gaige, 1926(Castroviejo-Fisher et al. 2012, and Adelphobates galactonotus (Steindachner, 1864) (Rojas et al. 2020). There are also cases of low genetic distances between distinct species, such as Pseudopaludicola jaredi Andrade, Magalhães, Nunes-de-Almeida, Veiga-Menoncello, Santana, Garda, Loebmann, Recco-Pimentel, underestimated. ...
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