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THERYA, 2019, Vol. 10 (2): 207-210 DOI: 10.12933/therya-19-776 ISSN 2007-3364
The vulnerable colombian weasel Mustela felipei (Carnivora): new
record from Colombia and a review of its distribution in protected
areas
Juan M. de Roux1, Elkin A. Noguera-Urbano2, Héctor E. Ramírez-Chaves3*
1 Ponticia Universidad Javeriana de Cali, Calle 18 # 118-250, Cali. Colombia. Email: juanderoux@yahoo.com
2 Instituto de Investigación de Recursos Biológicos, Alexander von Humboldt. Avenida Paseo Bolívar (Circunvalar) 16-20, Bogotá.
D.C., Colombia. Email: elkalexno@gmail.com
3 Departamento de Ciencias Biológicas, Facultad de Ciencias Exactas y Naturales, Universidad de Caldas, Manizales. Caldas,
Colombia. Email: hector.ramirez@ucaldas.edu.co (HRC)
* Corresponding autor
The Colombian weasel Mustela felipei is considered the rarest Neotropical carnivore only known from four localities in Colombia and one in
Ecuador. It is considered Vulnerable on the IUCN Red List along its distributional range. We present an unexpected photographic record of a
living specimen from Colombia that shed lights on its distribution on the Western Cordillera of Colombia, where it was previously known from
single a record obtained on 1986. This is the rst conrmed record of the Colombian weasel during the 21st century. Finally, we discuss the
species’ occurrence in protected areas of Colombia, to provide tools for the conservation of this rare species.
La comadreja colombiana Mustela felipei es considerada el carnívoro neotropical más raro, solo conocida de cuatro localidades en Colom-
bia y una en Ecuador. Se considera Vulnerable en la Lista Roja de la UICN a lo largo de su rango de distribución. Presentamos un registro foto-
gráco inesperado de un espécimen vivo de Colombia que arrojó luces sobre su distribución en la cordillera Occidental de Colombia, donde
anteriormente se conocía de un solo registro obtenido en 1986. Este es el primer registro conrmado de la comadreja colombiana durante el
siglo 21. Finalmente, discutimos la ocurrencia de la especie en áreas protegidas de Colombia, para proporcionar herramientas para la conser-
vación de esta especie rara.
Keywords Andes; Carnivora; photographs; rarity.
© 2019 Asociación Mexicana de Mastozoología,www.mastozoologiamexicana.org
Introduction
The Colombian weasel Mustela felipei (Carnivora: Musteli-
dae) is the smallest of all South American weasels (Ramírez-
Chaves and Patterson 2014). It is considered the rarest car-
nivore of South America based on its restricted distribution
(endemic to the Andes of Colombia and Ecuador), and low
population density (Ramírez-Chaves and Patterson 2014;
Ramírez-Chaves and Torres-Martínez 2016). It is known
from only ve localities and six specimens (Ramírez-Chaves
and Mantilla-Meluk 2009; Ramírez-Chaves and Patterson
2014). Globally, it has been categorized as “Vulnerable”
(VU; González-Maya et al. 2016), however, in Colombia, is
listed as ‘‘Endangered’’ mainly due to its restricted distribu-
tion and the habitat transformation of the areas in which
it has been registered (Mesa-González 2006; MADS 2017).
Little is known on this enigmatic species, with all informa-
tion coming from labels of museum vouchers, the most
recent collected on 1986 (Alberico 1994; Ramírez-Chaves
and Mantilla-Meluk 2009; Ramírez-Chaves et al. 2012;
Ramírez-Chaves and Patterson 2014). Morphological traits
on this rare species has been documented and can be used
to separate from its South American congenerics based on
its small size, short tail, darker coloration, and the presence
of a ventral spot on its chest or neck that is the same color
as the dorsum (Izor and de la Torre 1978; Ramírez-Chaves
and Mantilla-Meluk 2009; Ramírez-Chaves et al. 2014).
The Colombian weasel lacked photographs alive, either in
nature or in captivity (Ramírez-Chaves and Patterson 2014;
Suárez-Castro and Ramírez-Chaves 2015).
Material and methods
We report an unexpected record of a living specimen based
on photographs obtained on February 26, 2011, in the
main house of nca Morobia, located in the km 24 in the
Cali-Buenaventura road (3.544745° N, -76.615324° W, 1,780
masl). El Carmen, Dagua, department of Valle del Cauca,
Colombia. The identication was made based on its small
size, short tail lacking a black tip, darker coloration, and the
presence of a ventral spot on its chest or neck that is the
same color as the dorsum (Izor and de la Torre 1978).
The new locality is placed between the 1,750 and the
1,800 masl across the road from a relic of primary forest
(cloud forest); the climate is very humid and ranges from 10
to 25 °C. This forest extends to the south into the National
Natural Park Farallones de Cali. There is a very small moun-
tain stream that runs across nca Morobia, and it is located
about 100 m south of the main house.
In addition, with the new locality, we estimated the
Extent of Occurrence (EOO) and the Area of Occupancy
(AOO), based on a 2 km cell-width. We also tted an Eco-
logical Niche Model (ENM) using the six localities in Maxent
v 3.4.1 (Phillips et al. 2017). Maxent has been shown to out-
perform other algorithms, including when applied to small
208 THERYA Vol. 10 (2): 207-210
MUSTELA FELIPEI DISTRIBUTION
data sets (Elith et al. 2006; Pearson et al. 2007). We dened
our study area as a Minimum Convex Polygon plus a 2.5°
buer, to ensure that Maxent select the bioclimatic data
from ‘background’ pixels from a region in which known
records are more likely to form a representative sample of
the climatic conditions suitable for the species (Anderson
and Raza 2010). Environmental datasets were obtained at
30 seconds (~1 km2) resolution from the WorldClim Version
2 (http://worldclim.org/version2; Fick and Hijmans 2017),
and to avoid highly-correlated and redundant variables,
correlations between pairs of bioclimatic variables were
assessed using the Variance Ination Factor (VIF>10, Zuur et
al. 2010). The resulting 12 bioclimatic variables were used
to build the ecological niche model (BIO2 = Mean Diurnal
Range, BIO3 = Isothermality, BIO4 = Temperature Season-
ality, BIO5 = Max Temperature of Warmest Month, BIO6 =
Min Temperature of Coldest Month, BIO7 = Temperature
Annual Range, BIO11 = Mean Temperature of Coldest Quar-
ter, BIO13 = Precipitation of Wettest Month, BIO14 = Pre-
cipitation of Driest Month, BIO15 = Precipitation Seasonal-
ity, BIO18 = Precipitation of Warmest Quarter and BIO19 =
Precipitation of Coldest Quarter).
Since our sample sizes is low (six localities), we used
the linear and product features (see Phillips et al. 2006, and
Phillips and Dudík 2008 for recommendations regarding
sample sizes and features usage). We run the delete-one
jackknife modeling approach (Pearson et al. 2007; Shche-
glovitova and Anderson, 2013, called “n − 1 jackknife”), and
we estimated optimal model complexity considering sev-
eral regularization multipliers (0 to 2, by 0.5), using ENMeval
(Muscarella et al. 2014). Logistic output format was used to
describe the probability of presence or suitability (Phillips
and Dudík 2008), this is a continuous suitability map which
range between 0 (unsuitable) and 1 (the most suitable).
Then we applied the minimum training presence threshold
associated with any one of the observed records at the suit-
ability map to obtain a boolean map and representing the
potential distribution of the species. We report the accuracy
of the model using the average of the Area Under the Curve
(AUC > 0.75) of the Receiver Operating Characteristic (ROC)
curve based on the test records and considering AIC = 0
(Muscarella et al. 2014).
Results
The new record is based on an individual of M. felipei pho-
tographed by J. M. de Roux, while it was stuck in an out-
side bathroom. Back then, in 2011, the main house was
getting remodeled (the wooden oor was being lifted, and
the roong refurbished). The individual delivered a strong
odour (sort of like urine or musky) as it moved frantically,
looking for a way out. After taking the photographs, J. M.
de Roux left the door open for it to escape. The diagnostic
characters (e. g., the presence of a ventral spot on its chest
or neck, of the same color as the dorsum), are visible in
the photographs (Figure 1) casting no doubt on its correct
identication.
Figure 1. The Colombian weasel Mustela felipei alive from nca Morobia, Dagua,
Valle del Cauca, Colombia. Note the diagnostic characters: the dark coloration, short tail
without a black tip, and the presence of a ventral spot on its neck of the same color as the
dorsum. Photograph: J. M de Roux.
This is the second validated record of the species in
Western Cordillera and the rst near a protected area in this
Cordillera (Farallones National Natural Park). The locality is
close to the northernmost record at Alto de Galápagos, on
the limits between the departments of Chocó and Valle del
Cauca (Alberico 1994). With this new locality, the approxi-
mated Extent of Occurrence (EOO) is near to 40,146 km2, of
which 37,238 belong to Colombia. The Area of Occupancy
(AOO) is 24 km2 (based on a 2 km cell-width; Figure 2).
The t model (LQ0) had a very high (0.94) average test
and shows higher probabilities (Figure 1a) of the species
to occur in six departments of Colombia (Caquetá, Cauca,
Huila, Nariño, Risaralda and Valle del Cauca) and four prov-
inces in Ecuador (Carchi, Imbabura, Pichincha and Napo).
The potential distribution indicated that the species can be
found along the Western and Central range of the Colom-
bian Andes from Department of Antioquia to Department
of Nariño (Figure 2b). In Nariño we found an untypical
potential distribution, because there is a clear separation
Figure 2. a) Suitability model of the Colombian weasel Mustela felipei. b) Updated
potential distribution of M. felipei in South America. The star within the circle represents
the new locality in nca Morobia, Valle del Cauca, Colombia. The polygon (black line)
indicates the Extent of Occurrence (EOO) and black stars represent conrmed records.
www.mastozoologiamexicana.org 209
M. de Roux et al.
between the western and the eastern slopes of the Nudo
de los Pastos. According to the model, the potential dis-
tribution of the species extends from Carchi Province to
Chimborazo and Morona Santiago provinces in the Eastern
cordillera of Ecuador.
Discussion
The distribution of M. felipei has been previously stud-
ied (Burneo et al. 2009; Ramírez-Chaves and Mantilla-
Meluk 2009; Ramírez-Chaves and Patterson 2014), and
there were only five confirmed localities in Colom-
bia and Ecuador (Table 1). Other localities, including
records from Western Cordillera of Colombia (e. g., Avila
et al. 2017) have been proved to be wrong or impossible
to validate (Ramírez-Chaves et al. 2012; Ramírez-Chaves
and Torres-Martínez 2016). However, this record repre-
sents the sixth confirmed locality, and the first time the
Colombian weasel is photographed alive. Based on the
six confirmed localities, the AOO suggest that the spe-
cies should be assessed globally as Endangered (EN), as
is listed in Colombia (Mesa-González 2006).
The complete potential distribution of M. felipei com-
prises 82,659 km2. However, the Andean lands represent
the most impacted ecosystems of Colombia and one of the
most impacted in Ecuador (Harden 2006; Hofstede et al.
2002; Rodríguez Eraso 2013). Therefore, it is probable that
the available natural vegetation for the species is much
lower than the estimate potential distribution. M. felipei has
been only recorded in two protected areas in Colombia (the
rst was the National Natural Park Cueva de Los Guácharos,
in the Western Cordillera; Mesa-González 2006). The distri-
bution model shows a high probability of presence of the
Colombian weasel in a second protected area in the West-
ern Cordillera, the National Natural Park Munchique, which
is close to the locality of the new record, and in the Cen-
tral Cordillera, the Puracé National Natural Park. Two of the
previous records come from localities near to Puracé (Mesa-
González 2006). Although the Colombian weasel has not
been registered at Munchique yet, connectivity between
Farallones and Munchique protected areas is crucial for the
species’ persistence, and the creation of wildlife corridors
might represent an invaluable tool to enhance the eec-
tiveness of conservation strategies for this species.
Finally, this is the rst time that photographs provide
evidence on the presence of this rare carnivore during the
21st century (Table 1). The photographs were rstly avail-
able at the website iNaturalist, showing the relevance of cit-
izen science in providing useful information to the knowl-
edge of poorly known carnivores, as also has been shown
for other species (i. e., Gerstner et al. 2018).
Acknowledgements
We thank the Vicerrectoría de Investigaciones, Univer-
sidad de Caldas, and Bruce D. Patterson and the Science
and Scholarship Committee of the Field Museum of Natu-
ral History (FMNH), Chicago, for allowing us the access to
the information of specimens at the FMNH and support.
Thanks to BioModelos, an initiative that seeks to improve
the knowledge of the distributions of the species from
Colombia based on expert collaboration.
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Associated editor: Lia Méndez
Submitted: February 12, 2019; Reviewed: March 3, 2019;
Accepted: March 26, 2019; Published on line: March 21, 2019.