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Rediscovering the Apaporis Caiman (Caiman crocodilus apaporiensis): Notes from a Long-Anticipated Expedition


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Caiman crocodilus apaporiensis has been of particular interest because of its clearly differentiated morphotype within the Spectacled Caiman complex. Information on the biology of C. c. apaporiensis is incomplete because of its restricted distribution in the inaccessible middle and upper Apaporis River in Colombia. I undertook an expedition to the middle Apaporis River basin in an attempt to validate the presence of C. c. apaporiensis through observations on morphometry, ecology, and ethnozoology. Previously described skull characteristics were clearly differentiable in both adults and subadults in the region. However, because many individual C. c. apaporiensis that were either captured or visually assessed were relatively small, some skull characteristics more closely resembled the more general C. crocodilus morphotype. Although data on population size and distribution of C. c. apaporiensis remain limited, information gleaned from local inhabitants indicates that the subspecies is common in the middle Apaporis River. Population parameter and molecular phylogeography studies could lead to management practices that would protect the genetic integrity of C. c. apaporiensis by minimizing subspecific interbreeding.
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Rediscovering the Apaporis Caiman (Caiman crocodilus apaporiensis): Notes
from a Long-Anticipated Expedition
Author: Sergio A. Balaguera-Reina
Source: Journal of Herpetology, 53(4) : 310-315
Published By: Society for the Study of Amphibians and Reptiles
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Journal of Herpetology, Vol. 53, No. 4, 310–315, 2019
Copyright 2019 Society for the Study of Amphibians and Reptiles
Rediscovering the Apaporis Caiman (Caiman crocodilus apaporiensis): Notes from a
Long-Anticipated Expedition
Programa de Biologı´a Ambiental, Facultad de Ciencias Naturales y Matema´ticas, Universidad de Ibague´, Carrera 22 Calle 67, Ibague´ 730001, Colombia, and
Department of Biological Sciences, Texas Tech University, Lubbock, Texas, 79409, USA; E-mail:,
ABSTRACT.—Caiman crocodilus apaporiensis has been of particular interest because of its clearly differentiated morphotype within the
Spectacled Caiman complex. Information on the biology of C. c. apaporiensis is incomplete because of its restricted distribution in the
inaccessible middle and upper Apaporis River in Colombia. I undertook an expedition to the middle Apaporis River basin in an attempt
to validate the presence of C. c. apaporiensis through observations on morphometry, ecology, and ethnozoology. Previously described
skull characteristics were clearly differentiable in both adults and subadults in the region. However, because many individual C. c.
apaporiensis that were either captured or visually assessed were relatively small, some skull characteristics more closely resembled the
more general C. crocodilus morphotype. Although data on population size and distribution of C. c. apaporiensis remain limited,
information gleaned from local inhabitants indicates that the subspecies is common in the middle Apaporis River. Population parameter
and molecular phylogeography studies could lead to management practices that would protect the genetic integrity of C. c. apaporiensis
by minimizing subspecific interbreeding.
RESUMEN.—Caiman crocodilus apaporiensis ha sido de particular intere´s debido a que su morfolo´a esta´ claramente diferenciada
dentro del complejo de los caimanes de anteojos. La informaci ´
on en la biologı´a del C. c. apaporiensis esta incompleta debido a su
distribuci ´
on restringida en la regi ´
on media y superior del inaccesible rio Apaporis en Colombia. Emprendı´ una exploraci ´
on a la cuenca de
la regi ´
on media del rio Apaporis en un intento de validar la presencia del C. c. apaporiensis atrave´s de observaciones de morfometrı´a,
ecologı´a, y etno-zoologı´a. Las caracterı´sticas del cra´ neo descritas por Medem (1955) fueron claramente diferenciables en ambos adultos y
sub-adultos de la regi ´
on. Sin embargo, debido a que muchos de los C. c. apaporiensis que fueron capturados fueron relativamente
pequen˜os algunas de las caracterı´sticas craneales fueron ma´ s cercanas a la morfolo´a general del C. crocodilus. Aunque los datos de
poblaci ´
on y distribuci ´
on del C. c. apaporiensis permanecen limitados, la informaci ´
on recabada de los pobladores indica que la subespecie
es com ´
un a la mitad del rio Apaporis. Estudios sobre para´ metros de la poblaci ´
on y filogeografı´a molecular pueden concluir en practicas de
control que puedan proteger la integridad gene´tica de C. c. apaporiensis al minimizar la cruza dentro de la subespecie.
Colombia is one of the most biodiverse countries in the world
(Jenkins, 2003), as exemplified by the six species of crocodilians,
including three subspecies of the Spectacled Caiman (Caiman
crocodilus; Medem, 1981). However, information on the natural
history, distribution, and dynamic ranges of each of the
Colombian crocodilian species is scant to nonexistent (Mo-
rales-Betancourt et al., 2013; Balaguera-Reina et al., 2015a).
The Spectacled Caiman (C. crocodilus) has one of the broadest
distributions of all crocodilians, ranging from Mexico to Peru and
Brazil, with successful introductions by humans in the United
States (Florida), Cuba, and Puerto Rico (Velasco and Balaguera-
Reina, 2019). Caiman crocodilus has also been introduced into the
insular areas of San Andres and Gorgona Islands in Colombia
(Medem, 1981; Forero-Medina et al., 2006), with little to no
assessment of the ecological impacts on native species.
Morphological and genetic studies on C. crocodilus complex
have demonstrated considerable variability across its range,
supporting the recognition of at least four subspecies: C. c.
fuscus,C. c. crocodilus,C. c. chiapasius, and C. c. apaporiensis
(Medem, 1955, 1981; King and Burke, 1989; Busack and Pandya,
2001; Amato and Gatesby, 1994; Venegas-Anaya et al., 2008;
Escobedo-Galva´n et al., 2015). Caiman c. fuscus and C. c.
crocodilus are widely distributed in Central and South America,
whereas C. c. chiapasius and C. c. apaporiensis have more
restricted distributions (former: from Chiapas, Mexico to El
Salvador [Venegas-Anaya et al., 2008]; latter: endemic to the
middle and upper Apaporis River basins in Colombia [Medem,
The Apaporis Caiman (C. c. apaporiensis) has been of
particular interest since being collected by Medem in 1952 and
described in 1955 (=C. sclerops apaporiensis) because of its easily
differentiated morphotype (narrow snouted) within the Specta-
cled Caiman complex (Medem, 1955, 1981; Escobedo-Galvan et
al., 2015). The restricted distribution of C. c. apaporiensis and the
relative inaccessibility to middle and upper Apaporis River
basins to researchers due to protracted Colombian political
unrest have resulted in a paucity of research on this subspecies
for over 40 yr. A single published survey after Medem’s (1955)
work was conducted in the Apaporis River, recording 497
individuals across 11 areas in one-single-visit spotlight survey
(Naranjo, 1996; Rodriguez, 2000). However, only 42 individuals
were classified as C. c. apaporiensis, with 455 assigned to C. c.
crocodilus, lending to the uncertainty of both the presence and
conservation status of this endemic subspecies in the area. Thus,
clarifying the conservation and taxonomic status of the
Apaporis Caiman has become a prodigious challenge among
crocodilian biologists worldwide and was identified by the
International Union for Conservation of Nature/Species Sur-
vival Commission (IUCN/SSC)/Crocodile Specialist Group as
an issue in urgent need of resolution (Velasco and Balaguera-
Reina, 2019).
On the basis of starch gel electrophoretic analyses of blood
proteins from a single, alleged C. c. apaporiensis at the Cincinnati
Zoo, Densmore (1983) found this animal to be the most distinct
of all of the three C. crocodilus representatives that he sampled
(all but C. c. chiapasius). However, despite its unusual
appearance (extended snout), the absolute identity or origin of
the zoo specimen has never been verified. Some recent efforts to
DOI: 10.1670/19-028
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resolve the Apaporis Caiman taxonomic status genetically
(Bloor, 2013) and morphologically (Escobedo-Galvan et al.,
2015) during the last decade have failed because of the lack of
sufficient sample sizes and deoxyribonucleic acid (DNA) quality
(i.e., they extracted DNA from paratype skulls collected by
Medem in the 1950s), thereby limiting possible conclusions that
could be made. Recent debates among scientists regarding C. c.
apaporiensis taxonomic validity and its uncertain conservation
status have emphasized the need to resample the middle and
upper Apaporis River basins that were studied by Medem
(1955) to identify the distribution of potential subspecies.
Herein, I present results of an expedition carried out to the
middle Apaporis River basin to validate the presence of the
subspecies described by Medem (1955) with notes regarding its
ecology, ethnozoology, conservation, and possible future re-
Study Area.—The 1,060-km Apaporis River courses through
four departments (Guaviare, Caqueta´,Vaupe´s, and Amazonas) in
Colombia before emptying into the Caqueta´River(alsoknownas
Japura River; IDEAM et al., 2007). The Apaporis River originates
at the junction of the Tunia and the Ajaj ´u rivers at the Dos Rios
locality (between Caqueta´ and Guaviare departments) and flows
480 km until reaching the most prominent of its waterfalls, the
Jirijirimo waterfall, which acts as a zoogeographic barrier for
aquatic organisms (Medem, 1981). As a whitewater river, the
highly productive Apaporis River has high levels of suspended
sediments that result in near-neutral pH, high conductivity, and a
pale, muddy color (Sioli, 1984). The Apaporis River flows past
abandoned oxbows that may contain stagnant black waters that
are seasonally connected to the main river.
Fieldwork.—I carried out an expedition to the middle Apaporis
River basin between the Vaupes and Amazonas departments on
8–16 December 2018 (Fig. 1). I sampled five areas that included
the Inana, Churuco, and Arriba lagoons and two segments of the
Apaporis River between La Victoria and Inana lagoons and
between Inana and Churuco lagoons (Fig. 1). At night, I carried
out spotlight surveys (Chabreck, 1963) using handcrafted canoes
and a 5,000-lumen headlamp (InnoGear 5000 LED, Morgan Hill,
California) with assistance from two indigenous people who
powered the canoe with paddles. During the day, I interviewed
indigenous people to gain insights into the potential uses of, and
beliefs associated with, C. c. apaporiensis and into conflicts
FIG. 1. Study area highlighting the potential distribution area for Caiman crocodilus apaporiensis and all individuals seen across the five transects
followed at the middle Apaporis River basin, Colombia.
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between humans and the Apaporis Caiman and other crocodilian
species in the region. We did not collect personal information that
would reveal an interviewee’s identity and data derived from
interviews were kept anonymous in the analyses.
Night surveys were conducted between 1900 and 0400 h
along transects established in the five areas (Fig. 1, Table 1).
When an animal was visually located, I recorded location and
approached as close as possible to record morphological
features (relative snout width) as well as to estimate total
length (TL) and to obtain photographs. When possible, I
captured the animal by a noose with catch poles, individually
marked it by scale clipping, sexed it, and collected several
morphological measurements (snout–vent length [SVL], TL,
total head length, cephalic plate length, head height, fourth
maxillary tooth width, fourth mandibular tooth width, and
mass). In the case of animals where TL was estimated visually,
individuals were grouped by size classes as recommended by
Ayarzagu¨ ena (1983) for C. c. crocodilus as follows: classes I (<50
cm), II (50–120 cm), III (121–180 cm), and IV (>180 cm). Each of
the five study areas was sampled once and captured animals
were released immediately after the collection of data. Descrip-
tive statistical and morphological data were analyzed via R 3.5.2
(R Development Core Team, 2012). Finally, a first approximation
of C. c. apaporiensis distribution map was accomplished using
ArcGIS 10.6 (ESRI, 2017) on the basis of the IUCN Red List
protocol using hydroSHEDS (Lehner et al., 2008; IUCN, 2012).
A total of 105 C. c. apaporiensis and 1 Paleosuchus palpebrosus
were recorded across the five surveyed areas (Figs. 1, 2) and of
these, 69 were registered as eyes only—without a TL estimate—
and 17 individuals were captured with the full complement of
measurements obtained. The TLs of 19 individuals were
estimated only visually without capture and were grouped as
class II (10 individuals), class III (seven individuals), and class
IV (two individuals). A size class analysis including all animals,
both captured and sighted, for whom TL was estimated (N=
37) showed a large number of juveniles (class II) and few adults
(class IV) across the study area (Fig. 3).
Laguna Arriba had the highest number of C. c. apaporiensis
recorded (55 individuals; Table 1) and was the only site with a
record of P. palpebrosus. Churuco and Inana´ lagoons had
intermediate numbers of C. c. apaporiensis (24 and 17 individ-
uals, respectively). The river segments, Victoria-Inana´and
Inana´ -Churuco, had lower numbers (seven and two individuals,
respectively), with no presence of P. palpebrosus. The relative
abundance estimates for transects visited were 8.21 individu-
als/km in Laguna Arriba, 6.15 individuals/km in Churuco
Lagoon, 4.86 individuals/km in Inana´ Lagoon, 1.84 individu-
als/km in the La Victoria–Inana´ River segment, and 0.25
individuals/km in the Inana´–Churuco River segment (Table 1).
Captured animals had TL and SVL measurements averaging
68.5 642.2 cm and 35.1 622.3 cm, respectively, with a mean
body mass of 3 kg (min.–max. =0.09–27.8 kg; Table 2). One
individual captured at the Inana´-Churuco River segment was
not included in this descriptive analysis because it did not have
the single-crested part of the tail, a condition that appeared to be
genetic or developmental rather than a mutilation caused by
another animal. Seven individuals were males, three were
females, and seven were of undetermined sex. Five of the latter
animals were observed at a single location in the Arriba Lagoon
with TL between 35 and 40 cm (i.e., yearlings; Table 2).
On the basis of the historically reported ranges of C. c.
apaporiensis (Medem 1955, 1981; Naranjo, 1996) plus those
collected in the present study, I estimate the distribution area of
the C. c. apaporiensis to be 12,640 km
, covering a total of 14
watersheds across the upper and middle Apaporis River,
including the lower Ajaj ´u, Tunia, Mecaya, and Tucunema river
basins (Fig. 1).
Ethnozoology.—I interviewed 11 indigenous people (all adults
>30 yr old) from La Victoria community (total population =96;
Appendix 1). All were born in the area and were members of the
various indigenous tribes (Barasano, Cubeo, Tatuyo, Carapana,
Cabiyari, Yucuna, Carijonas, and Tucanos, among others). The
local indigenous people recognized three crocodilian species, or
‘cachirres,’’ in the area: two darkly colored species (‘‘cachirres
negros’’; Paleosuchus trigonatus and P. palpebrosus) and one more
lightly colored species (‘‘cachirre blanco’’; C. c. apaporiensis). Most
indigenous communities in the area preferred to eat black over
white cachirres. People of only three tribes consume white
cachirres (Barasanos, Macunas, and Letuamas), with most of
these individuals inhabiting one nearby community (Mu-
tanacua). Other tribes, especially those living in La Victoria, do
not use white cachirres as a food source because of either
religious beliefs (white cachirres represent condemned men),
tradition as dictated by elders, or because of bad taste with a
slimy nature to the meat. Only 2 of the 11 individuals interviewed
TABLE 1. Transects sampled across the middle Apaporis River basin
and some lagoons around this area. Inana´ and Churuco lagoons were
the areas sampled by Medem (1955).
Transect name
No. of
Caiman crocodilus
La Victoria–Inana´
(Apaporis River
3.8 7 1.84
Inana´ –Churuco
(Apaporis River
8.1 2 0.25
Laguna Arriba 6.7 55 8.21
Churuco Lagoon 3.9 24 6.15
Inana´ Lagoon 3.5 17 4.86
Total 26 105
FIG. 2. Heads of Caiman crocodilus apaporiensis captured in the middle
Apaporis River basin, Colombia. Scales on each side and labels
represent the total head length (THL) in centimeters of each animal
depicted. 4MTW, fourth mandibular tooth width; 4XTW, fourth
maxillary tooth width; CPL, cephalic plate length.
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reported hunting white cachirres and using them as bait or to
feed hunting dogs.
My interviews indicated that December is the primary mating
season for white cachirres, with eggs laid in January and
hatching occurring between March and April. The individuals
reported that white cachirres are abundant in lagoons and
closed water bodies, with lower densities in the flowing rivers
and open areas. In contrast, black cachirres were considered to
be scarce across all areas, likely caused by excessive use by
On the basis of my interviews, hunting that focused on
acquiring white cachirres skins came to the area in the mid-
1960s when rubber tappers (mainly foreigners) started to buy
skins from the local people. The most valuable skins at the time
were jaguar, ocelot, otter, and white cachirres. Hunting pressure
ceased in the 1980s when the profitable coca fields (Erythrox-
ylum coca) were established in the area.
I verified the presence of the Apaporis River caiman in five
areas where Medem (1955) described the subspecies for the first
time in the middle basin of the Apaporis River, with no
sightings of any other C. c. crocodilus morphotypes. My
corroboration of the subspecies was based on both skull
(comparatively narrow snout and flat cranial table) and external
morphology (bright yellow-brownish color spotted with black
vermiculations) as described by Medem (1955). The observation
is highly relevant because Naranjo (1996) reported a high
proportion of animals with C. c. crocodilus morphotype and
Medem (1981) hypothesized that C. c. crocodilus was colonizing
the upper Apaporis River basin in the 1970s as a result of
hunting pressure in the Caqueta River. One singular feature
found in animals captured in the present study, and also by
Medem (1955), was the presence of several orange-colored
scutes on the side of the neck that have not been reported in any
TABLE 2. Morphometric variables measured for all individuals captured across transects in the middle Apaporis River basin: snout–vent length
(SVL), total length (TL), total head length (THL), cephalic plate length (CPL), head height (HH), fourth maxillary tooth width (4XTW), fourth
mandibular tooth width (4MTW).
Identification SVL (cm) TL (cm) THL (cm) CPL (cm) HH (cm) 4XTW (cm) 4MTW (cm) Weight (kg)
2 40 75 10.8 4 4 4
4 28 59 8 3 3 3 2 0.61
5 38.5 68.5 10 5 3.5 3.5 2.6 1
6 31.6 64 9.2 4.3 3.2 3.2 2.5 0.8
8 39 78.8 10.8 4 3.9 4 2.6 1.47
9 17.5 35.2 5.3 2.4 2.3 2.3 2 0.09
10 59 116 16.2 5 5.2 5.2 3.7 4.79
11 45 85 12.8 4.5 4.2 4.5 3.3 2.56
12 102 195 27.2 8.3 9.8 10 5.6 27.8
13 65 127 17.5 6 7 6 4.2 7.39
14 16.4 35 5 2 2 1.8 1.4 0.16
15 17.6 36.8 5.3 2.9 2 2.7 1.4 0.17
16 19 40 5.5 2.5 2.3 2.6 1.5 0.17
17 17 36.5 5 2.4 2 1.8 1.3 0.12
18 16.8 36 5.2 2.2 2 2.3 1.3 0.21
19 16.8 35 5.3 2.4 2.1 1.7 1.3 0.1
Mean 35.58 70.18 9.94 3.81 3.66 3.66 2.45 3.16
SD 22.87 42.88 5.94 1.65 2.08 2.03 1.23 6.89
Max. 102 195 27.2 8.3 9.8 10 5.6 27.8
Min. 16.4 35 5 2 2 1.7 1.3 0.09
FIG. 3. Size class analysis depicting the proportions of juveniles and subadults (classes I and II) compared with reproductively mature animals
(classes III and IV). Given the life history of crocodilians with a type III survivorship curve (low proportion of individuals surviving in the first stages
of life; Milnes and Guillette, 2008), one should expect a large number of adults and fewer juveniles in a nonaffected population.
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other subspecies of the C. crocodilus complex. One possible
explanation of orange-colored scutes could be discoloring due
to exposure to iron or other chemicals that can stain the skin.
Skull characteristics described by Medem (1955) as unique in
Apaporis Caimans were clearly differentiable in both adults and
subadults (Fig. 2). However, as many animals captured or
spotted visually were smaller (i.e., juveniles and yearlings),
skull characteristics more closely resembled the more general C.
crocodilus morphotype, an observation also made by Medem
(1955). The young C. c. apaporiensis with C. crocodilus morpho-
type features could explain the high number of C. c. crocodilus
reported by Naranjo (1996). Therefore, C. c. crocodilus may not
actually occur in the area. Genetic analyses are ongoing to fully
clarify the phylogeographic relationship between C. c. apapor-
iensis and C. c. crocodilus because of the significant variation in
skull dimensions (narrow snout vs. broad snout) that has been
reported for C. c. crocodilus across its range (Ayarzagu¨ ena, 1983;
Gorzula, 1994; Ayarzagu¨ ena and Castroviejo, 2008).
All individuals over the range of body sizes were very wary
of humans across all areas surveyed, with the exception of
Laguna Arriba, likely reflecting some type of hunting pressure
in these other localities. A ‘‘hunting-induced wariness’’ hypoth-
esis was supported by locals who reported that some tribes in
the area consume Apaporis Caimans. A size class analysis was
consistent with the hypothesis in that there were a large
proportion of juveniles and very few adults present in the
samples (Fig. 3). Given the life and reproductive history of
crocodilians (type III survivorship curve, with low proportion of
individuals surviving in the first stages of life; Milnes and
Guillette, 2008), one should expect a large number of adults and
fewer juveniles in a nonaffected population. Even though C. c.
apaporiensis is adapted to endure high mortality in early ages
and low mortality in the older ones, high hunting pressure in
adults could put populations at risk.
The largest male and female C. c. apaporiensis captured in my
study were 195 cm and 85 cm TL, respectively, which contrasts
with the maximum sizes reported for the subspecies across the
upper and middle Apaporis River basins (222 cm TL for males
and 173 cm TL for females; Medem, 1981). Observed differences
between my study and that of Medem (1981) could be
influenced by variables such as the reproductive patterns of
the species as well as environmental features such as precipi-
tation and temperature (Brien et al. 2008; Balaguera-Reina et al.,
2016). The reproductive ecology of the Apaporis Caiman is
poorly understood and many of the descriptions are based on
data collected by third parties (i.e., local people). Only Medem
(1981) reported a partially constructed nest in March, 1952 at the
Inana´ Lagoon. The observation of five putative yearlings (TL
~35–40 cm), grouped at the same place in the Laguna Arriba,
likely indicates the presence of a nesting area in the vicinity.
Medem (1955) described the distribution of this subspecies to
range between Yaviya Port (rubber camp) and Jirijirimo
Waterfalls, indicating that it was somewhere around 200 km.
The distribution of the subspecies was later expanded upon
finding the Apaporis Caiman at the Ajaju River mouth where
the Apaporis River is born (Medem, 1981). On the basis of these
data and using the Red List range protocol (IUCN, 2012), I
estimate a total distribution area of 12,640 km
for the
subspecies (Fig. 1). Even though this approximation may
overestimate the actual range of the subspecies (because of the
inclusion of uninhabitable areas), it provides an initial spatial
analysis that can be used as the null hypothesis to test in future
studies. It also strongly implies that more expeditions to the
upper and middle Apaporis River basins must be undertaken to
clarify the actual range of C. c. apaporiensis on the basis of more
robust analyses (e.g., species distribution models).
Although the number of scientific expeditions to the region
has been comparatively low and the population size and range
of the subspecies remain largely unknown, data reported by
researchers and locals seem to suggest that the subspecies is
common in the middle Apaporis River. The persistence of
morphotype is critical because of the necessity of taxonomically
clarifying its status. Scientific efforts must be directed at the
upper Apaporis River basin to assess population parameters
(growth, demographics, densities, spatial dynamics) as well as
the phylogeography of the subspecies because of the possibility
of subspecific intergradations (e.g., C. c. crocodilus with C. c.
apaporiensis), which could be to the detriment of C. c. apaporiensis
genetic integrity. Ultimately, detailed information on the biology
of C. crocodilus in the region will aid in resolving the subspecific
vs. specific status. Finaly, a clear definition of the conservation
status of the subspecies will allow government agencies to
facilitate the passing of up-to-date legislation to preserve and
sustainably use the Apaporis Caiman.
Acknowledgments.—My project was sponsored by the Univer-
sity of Ibague, Texas Tech University, IUCN/SSC/Crocodile
Specialist Group, CrocFest, and CrocDocs and was approved by
the University of Ibague research center (18-489-ESP) to capture
Apaporis Caimans and collect samples under its national
permit. I thank Alfredo Vargas-Carapana and his family for
hosting me and helping me to navigate and explore the
Apaporis River ecosystems and cultures. I also thank Lou
Densmore, Lorena Carvajal, Mario Vargas, Jarvi Vargas, and
Johnatan Vargas for their help in the field and improving this
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APPENDIX 1. Main content of the questionnaire used on the survey in both English and native (Spanish) languages.
No. Questions Responses
1 How many crocodilian species can you identify in the area? Open
¿Cua´ ntas especies de cocodrylidos se ven en el a´rea? Abierta
2 How do you call these species? What names do they have? Open
¿C ´
omo llamas a estas especies? ¿Tienen alg ´un nombre en particular? Abierta
3 Where and when do you see white and black cachirres? Open
¿D ´
onde y cua´ ndo ves cachirres blancos y negros? Abierta
4 Where and when do you see white and black cachirres nesting? Open
¿D ´
onde y cua´ ndo ves cachirres blancos y negros anidando? Abierta
5 Where and when do you see white and black cachirres babies? Open
¿D ´
onde y cuando ves pichones de cachirres blancos y negros? Abierta
6 White and black cachirres populations in the area are increasing, decreasing, or the same
compared with 20 years ago Open
Comparado con lo visto hace 20 an˜ os, ¿la cantidad de cachirres blancos y negros ha
aumentado, disminuido o siguen igual? Abierta
7 Are white and black cachirres hunted in the area? Which ones? Reasons? Open
¿Cazan cachirres blancos y/o negros en el a´ rea? ¿Cua´les especies? ¿Cua´l es la principal raz ´
para cazarlos? Abierta
8 Do you think white and/or black cachirres are special creatures? Any belief around them? Open
¿Tienes alguna creencia en particular sobre los cachirres? Abierta
9 Could you explain to me what is the cachirres’ hunting history in the area? Open
¿Podrı´as contarme un poco sobre c ´
omo ha sido hist ´
oricamente la cacerı´a de cachirres en el
a´ rea? Abierta
10 What type of conflicts have you had with cachirres in the area? Open
¿Que´ tipo de conflictos o problemas ha tenido con los cachirres? Abierta
Age of respondent Open
Gender of respondent Open
Tribe of respondent Open
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... Entonces, en 2018, Balaguera-Reina (2019) El ejemplar recolectado en el presente trabajo es un juvenil (Figura 3g); por su coloración, que es amarillo oscuro y la forma del rostro que no es angosto se parece más a los ejemplares de otras poblaciones del complejo C. crocodilus. Cabe aclarar que las características morfológicas en los juveniles de C. c. apaporiensis no son claras para poder realizar una determinación más precisa (Medem 1955, Balaguera-Reina 2019. ...
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Resumen El inventario de anfibios y reptiles en la cuenca del río Apaporis se realizó en el marco de la iniciativa Colombia BIO (Minciencias); el esfuerzo de muestreo se centró en las localidades de Buenos Aires y Cerro Morroco, cuenca media del río Apaporis; en Cerro Azul-Cerro Campana, cuenca alta, y en el raudal de Jirijirimo. A partir de la búsqueda en bosques, aflo-ramientos rocosos y raudales se reportan 41 especies de anfibios de los cuáles se destaca el registro de una familia nueva para el país, Ceuthomantidae y una especie indescrita, la confirmación de la pre-sencia de O. vilarsi en Colombia y el hallazgo de otra especie de la familia Craugastoridae por describir. En reptiles se encontraron 33 especies, se recolectaron ejemplares de algunas poco conocidas o que tienen una distribución relativamente pequeña en la parte noroccidental de la Panamazonia y muy relacionadas con el Escudo Guayanés. Se destacan los registros de Bachia pyburni, Neusticurus medemi, Helicops hagmanni y la tortuga Rhinemys rufipes. Abstract The inventory of amphibians and reptiles in the Apaporis River basin was carried out within the framework of the Colombia BIO initiative (Minciencias). The sampling effort was focused on the towns of Buenos Aires and Cerro Morroco, in the middle basin of the Apaporis River; in Cerro Azul-Cerro Campana, upper basin, and in the Jirijirimo torrent. The search in forests, rocky outcrops, and torrents allowed the report of 41 species of amphibians, of which the record of a new family for the country, Ceuthomanti-dae, an undescribed species, the confirmation of the presence of O. vilarsi in Colombia, and the discovery of another species of the Craugastoridae family yet to be described stand out. 33 species of reptiles were found, and some little-known specimens or with a relatively small distribution in the northwestern part of the Pan-Amazon and closely related to the Guiana Shield were collected. The records of Bachia pyburni, Neusticurus medemi, Helicops hagmanni and the turtle Rhinemys rufipes stand out.
... Population ecology studies on spectacled caimans in Colombia have been highly concentrated on regions such as the Caribbean (Barahona et al. 1996, Ulloa and Cavanzo 2003, Cavanzo 2004 (Forero-Medina et al. 2006), and the Amazon (Naranjo 1996, Balaguera-Reina 2019. Most of these studies were performed across periods of time less than a year, which implies they were missing at least part of the story due to the effects of environmental annual cyclical variables (e.g., temperature, precipitation) on population parameters (e.g., number of individuals, demographic structure; Balaguera-Reina et al. 2018). ...
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Population ecology studies on spectacled caimans (Caiman crocodilus) in Colombia have been few and far between with many covering short periods and defining population parameters based on relative indices (i.e., individuals/km). This reflects a lack of information on the general effects that environmental variables have on annual cycles of population dynamics, as well as a bias in abundance estimations due to the uncertainty of detection error. Keeping this in mind, we assessed the abundance and demographic structure of the spectacled caiman population inhabiting the Apaporis River middle basin over a year, based on robust hierarchical model that accounts for imperfect detection. We recorded a total of 1156 caiman observations between December 2018 and November 2019, estimating an average predicted value for abundance across all surveys of 29.99 ± 13.17 individuals, slowly increasing as the transect length increases and increasing variation as months passed by. The average detection probability was 0.69 ± 0.25 across all surveys, with no apparent effect as water temperature and relative humidity change across space-time and slowly decreasing as months go through. The population size estimated based on the top-performing model was 1763 ± 786 caimans across ~7.1 km2 assessed. We estimate the commonly used relative abundance (encounter rate) index as well as a generalized linear model and discuss how those relate with the values predicted by N-mixture models. We also discuss the relevance and cautions researchers should have when using N-mixture models to better understand spectacled caiman ecology.
The spectacled caiman (Caiman crocodilus) is currently considered to be a species complex due to the relatively high morphological and molecular diversity expressed across its range. One of the populations of interest, inhabiting the Apaporis River (Colombia), was described based on skull features as an incipient species (C. c. apaporiensis) and has been treated by some authors as a full species. Recent molecular work challenged this hypothesis, because relatively low mitochondrial molecular differentiation was found between the morphologically described Apaporis caiman and C. crocodilus (s.s.) Amazonian populations. Here, we present an update on the topic based on a larger molecular sample size and on analysis of expanded geometric morphometric data that include six newly collected skulls. Morphometric data support the existence of previously recognized morphotypes within the complex in Colombia and demonstrate that the newly collected material can be assigned to the classic Apaporis caiman morphotype. However, our expanded genetic analysis fails to find appreciable mitochondrial molecular divergence of the Apaporis caiman population from the C. c. crocodilus population (COI-CytB: Amazon Peru 0.17 ± 0.06%, CytB-only: Caquetá River Colombia 0.08 ± 0.07%). The Apaporis caiman is interpreted to be a phenotypically distinct member of the cis-Andean C. crocodilus metapopulation that has not yet achieved (or may not be undergoing at all) appreciable genetic differentiation. Thus, it should not be considered a fully independent evolutionary lineage, nor given full species rank.
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Caiman crocodilus is a species of alligator that is distributed throughout the American continent, from the southern United States to the north of Bolivia. It currently has three valid subspecies C. crocodilus fuscus, C. crocodilus chiapasius and C. crocodilus crocodilus, because it was recently described that the subspecies C. crocodilus apaporiensis really is a morphological variation of the subspecies C.c. crocodilus. This species is commonly called as ‘’ spectacled caiman’’ due to the edge that forms in the anterior part of its eyes, in Colombia it is known as ‘’Babilla’’ and is usually recognized in practically all the departments of the country due to its commercial use and its extensive distribution. Despite the recognition of the species throughout the territory, its study focuses on production, trade, and use, leaving aside its study in wild populations and its interaction and importance in the habitats in which it is present, therefore, a bibliographic review is necessary to evaluate the state of knowledge of the species in Colombia and effectively understand the key points for its use and conservation. To achieve this, an exhaustive review of databases, research tools, web pages, software was carried out and a map of the current distribution of the species was generated. 198 documents associated with the species were collected and divided into the following categories: general, application and use, conservation, distribution, ecology and systematics. Most of the information was associated with the category of application and use. The results indicate that most of the documents at the regional level come from the Caribbean, where zoocria processes are largely developed. It seems that the main interest generated by the species is its commercial value which makes it essential to prioritize studies in the wild because, although the species is not threatened, its historical mismanagement could be affecting its conservation.
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Studies on the biology of Caiman crocodilus have drawn attention to its biology with emphasis on systematic, taxonomy and ecology. However, anatomical aspects, such as skull characteristics, have not been studied in detail throughout its geographic range. In this study the skull characteristics for C. crocodilus subspecies, C. c. fuscus, C. c. chiapasius, C. c. crocodilus, and C. c. apa-poriensis were analyzed using geometric morphometrics and descriptive morphology, including geographic and ontogenetic variation. Variation in skull morphology was found between the subspecies analyzed. Trans-Andean subspecies, C. c. fuscus and C. c. chiapasius, exhibit breviros-trine skulls but they are different in the contact between frontal and nasal bones and the size of the palatine process of the maxilla; therefore, populations in Colombia correspond to C. c. fuscus and, C. c. chiapasus is not distributed in Colombia. Although cis-Andean subspecies, C. c. apaporiensis and C. c. crocodilus, have longirostrine skulls, both subspecies differ in the shape of the skull and in osteological characters; then, adults of C. c. apaporiensis present frontal and nasal in contact and, V-shape maxillary-premaxillary suture; while C. c. crocodilus specimens exhibit a high geographic and ontogenetic variation, supporting the hypotheses that there at least two clades of such subspecies for Colombia. These morphological differences should be considered in future systematics studies and policies on global conservation of the different C. crocodilus subspecies.
The order Crocodylia contains the sole reptilian survivors of the Archosauria, which also includes the dinosaurs and birds. While the living forms are not nearly as diverse as they have been in the past, they represent a lineage that first appeared in the Mesozoic Era, and that has successfully survived a number of extinction events. They also represent a group that has been seriously impacted by humans, both in terms of hunting and habitat destruction. Crocodylyians are, therefore, largely protected or endangered. However, they are critical apex predators that often serve as ‘keystone’ species and indicators of the health of the environments that they inhabit. Key Concepts The Crocodylia (the only living non‐avian Archosaurs) are aquatic or semi-aquatic apex predators that can trace their origins to the early Mesozoic Era. The three recognized families, Alligatoridae, Crocodylidae and Gavialidae, are currently represented by some 30 named forms found primarily in tropical or subtropical environments. The combination of human hunting for their meat and skins, habitat loss and long generation times have contributed to the threatened or endangered status of many living crocodylians. Even though most recognized species seem to be valid hybridization, especially within the genus Crocodylus, is common and complicates efforts to understand their recent evolutionary history; growing evidence among several caiman species suggests that hybridization is more prevalent than previously thought. Molecular analyses in conjunction with assessments of morphological variation and paleontology are contributing to a more accurate understanding of crocodylian phylogeny, particularly within Crocodylidae and Gavialidae.
Advances in molecular biology and genetics are revealing that many recognized crocodylian species are complexes of two or more cryptic species. These discoveries will have a profound impact on interpretation of the crocodyliform fossil record. Our understanding of ranges of intraspecific variation in modern crocodylian morphology may be based on multiple species and thus express both intraspecific and interspecific variation. This raises questions about our ability to recognize modern species in the fossil record, and it also indicates that specimens from disparate localities or horizons may represent not single widespread species, but multiple related species. Ranges of variation in modern species require a thorough re-evaluation, and we may have to revisit previous perceptions of past crocodyliform diversity, rates of evolution or anagenetic lineages in stratigraphic succession. These challenges will not be unique to those studying crocodyliforms and will require sophisticated approaches to variation among modern and fossil specimens.
The Apaporis caiman (Caiman crocodilus apaporiensis) has been of particular interest due to its highly differentiated morphology. However, no molecular research has been done to clarify its taxonomy. We characterized the genetic variation within C. crocodilus by assessing the evolutionary trajectory of Apaporis caiman populations using mitochondrial molecular markers. We collected ten Apaporis caiman samples from the middle basin of the Apaporis River, Colombia, sequenced two mitochondrial genes [cytochrome oxidase I (COI) and cytochrome B (CytB)], and analysed them together with all available sequences from homologous gene fragments at GenBank for the species. Phylogenetic reconstructions revealed three main clades clearly differentiated across the C. crocodilus complex. These clades matched genetically and geographically with three of the four subspecies currently recognized (C. c. chiapasius, C. c. fuscus and C. c. crocodilus). However, we found low to almost non-existent genetic differentiation between C. c. crocodilus and the until-now morphologically recognized C. c. apaporiensis, suggesting that the latter is part of the genetic spectrum present within C. c. crocodilus. We reject the hypothesis of an expected elevated level of genetic variation due to isolation (supported by morphological differentiation) and support the idea of Apaporis caiman populations as a C. crocodilus ecomorph.
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Conservation of large predators has long been a challenge for biologists due to the limited information we have about their ecology, generally low numbers in the wild, large home ranges and the continuous expansion of human settlements. The American crocodile (Crocodylus acutus) is a typical apex predator, that has suffered from all of these characteristic problems, especially the latter one. Humans have had a major impact on the recovery of this species throughout its range, even though most of the countries it inhabits have banned hunting. The last decade has made it clear that in order to implement sound conservation and management programs, we must increase our understanding of crocodile spatial ecology. However, in only two countries where American crocodiles have telemetry studies even been published. Herein we have characterized the spatial ecology of C. acutus on Coiba Island, Panama, by radio-tracking (VHF transmitters) 24 individuals between 2010 and 2013, to determine movement patterns, home range, and habitat use. We have then compared our findings with those of previous studies to develop the most comprehensive assessment of American crocodile spatial ecology to date. Females showed a higher average movement distance (AMD) than males; similarly, adults showed a higher AMD than sub-adults and juveniles. However, males exhibited larger home ranges than females, and concomitantly sub-adults had larger home ranges than juveniles, hatchlings, and adults. There was an obvious relationship between seasonal precipitation and AMD, with increased AMD in the dry and "low-wet" seasons, and reduced AMD during the "true" wet season. We found disaggregate distributions according to age groups throughout the 9 habitat types in the study area; adults and hatchlings inhabited fewer habitat types than juveniles and sub-adults. These sex- and age-group discrepancies in movement and habitat choice are likely due to the influences of reproductive biology and Coiba's precipitation cycle. Juveniles also showed distinct movement patterns and home ranges; however, with sexual maturation and development, these behaviors became more characteristic of adults and sub-adults. Ours is one of a very small number of studies that will allow future management and conservation planning to be based on the comprehensive integration of the spatial ecology of a Neotropical crocodylian apex predator.
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Caiman crocodilus and C. yacare are economically valuable species afforded legal protection both within the United States and around the world. While five populations of these species have received formal taxonomic recognition between 1758 and 1955, there has never been an analysis of variation across populations representing the entire range of these species. We examined 13 external morphological characteristics in 360 individuals from known localities distributed throughout the range of these taxa. Using covariance, principal component and discriminant function analyses, we find no defensible basis for the partition of C. crocodilus into subspecies, nor do we feel that considering C. yacare a subspecies of C. crocodilus, as proposed by some, is warranted. The implication of these findings for enforcement of current legislation is discussed.
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Wildlife species have been recognized as sentinels of environmental health for decades. In fact, ecological data on various wildlife populations provided the impetus for banning some organochlorine pesticides over the last few decades. Alligators are important sentinels of ecosystem health in the wetlands of the southeastern United States. Over the last 15 years, a series of studies have demonstrated that environmental exposure to a complex mixture of contaminants from agricultural and municipal activities alters the development and functioning of alligators' reproductive and endocrine systems. Further studies of basic developmental and reproductive endocrinology in alligators and exposure studies performed under controlled laboratory conditions support the role of contaminants as causal agents of abnormalities in gonadal steroidogenesis and in reproductive tract development. These studies offer potential insight into environmentally induced defects reported in other wildlife and human populations exposed to a wide array of endocrine-disruptive contaminants.
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We radio-tracked five male and eight female estuarine crocodiles (Crocodylus porosus) in a non-tidal waterhole in Lakefield National Park in northern Queensland during the late dry/mid-wet season (2003-04) and the following dry season (2004). Individual crocodiles occupied larger home ranges (River Channel Areas (RCA) during the late dry/mid-wet season (10.64 ± 2.86 ha) than in the dry season (3.20 ± 1.02 ha), and males occupied larger home ranges (23.89 ± 2.36 ha) than females (5.94 ± 1.34 ha) during the late dry/mid-wet season. There were no obvious differences in home range between sexes during the dry season. During the late dry/mid-wet season, adult males often travelled long distances along the waterhole while females moved less. During the dry season, movement patterns were quite variable, with no clear difference between sexes. All crocodiles were most active from late afternoon (1500-1800 hours) until midnight. Individual home ranges (RCA) overlapped considerably during the late dry/mid-wet season. The extent of home-range overlap between three adult males and the number of times they either passed each other or were located near each other was particularly striking. Previous research has come to conflicting conclusions about the extent of territoriality in wild estuarine crocodiles, although it has been widely believed that males are highly territorial. The findings imply that large adult male estuarine crocodiles are not highly territorial in non-tidal freshwater systems that are geographically confined.
Caiman crocodilus apaporiensis has been considered by several authors as an extreme of morphological variation within the Caiman crocodilus complex. Here, we evaluate its position in the Caiman crocodilus complex morphospace using morphological traits from head shape. We examined the holotype and seventeen paratypes of Caiman crocodilus apaporiensis Medem 1955 deposited at the Field Museum of Natural History. We performed multivariate morphometric analyses: principal component analysis (PCA) and discriminant function analysis (DFA), based on 21 cranial traits of of C. c. apaporiensis, C. yacare and the C. crocodilus complex (C. c. chiapasius, C. c. fuscus andC. c. crocodilus). We find a notable separation of C.c. apaporiensis from C. yacare and C. crocodilus complex in the morphospace. We suggest that geographic isolation might have driven this morphological separation from the C. crocodilus complex, but further analysis are necessary to confirm whether these differences are related with genetic differentiation within the complex. In addition, we suggest that environmental heterogeneity might drive the evolution of independent lineages within the C. crocodilus complex.
Attempts to assess the natural affinities and evolution of living crocodilians have been difficult and largely contradictory (Kalin, 1955; Steel, 1973; Dowling and Duellman, 1974). Morphological character analysis has been misleading due to the overall conservatism of these reptiles and to the tendencies toward parallelism and convergence of traits that has occurred during their evolution (Langston, 1973). These complications, together with the lack of critical fossils, have made paleontological interpretations extremely difficult (Sill, 1968; Hecht and Malone, 1972; Langston, 1973; Buffetaut, 1979). Because of such problems and the small number of living species, morphoclines are rare, further complicating the efforts of the comparative morphologist (Hecht and Malone, 1972).
To study the Earth system and to better understand the implications of global environmental change, there is a growing need for large‐scale hydrographic data sets that serve as prerequisites in a variety of analyses and applications, ranging from regional watershed and freshwater conservation planning to global hydrological, climate, biogeochemical, and land surface modeling. Yet while countless hydrographic maps exist for well‐known river basins and individual nations, there is a lack of seamless high‐quality data on large scales such as continents or the entire globe. Data for many large international basins are patchy, and remote areas are often poorly mapped. In response to these limitations, a team of scientists has developed data and created maps of the world's rivers that provide the research community with more reliable information about where streams and watersheds occur on the Earth's surface and how water drains the landscape. The new product, known as HydroSHEDS (Hydrological Data and Maps Based on Shuttle Elevation Derivatives at Multiple Scales), provides this information at a resolution and quality unachieved by previous global data sets, such as HYDRO1k [ U.S. Geological Survey (USGS) , 2000].