ArticlePDF Available

Abstract and Figures

The dwarf coati (Nasua nelsoni) is an endemic mammal to Cozumel Island, Quintana Roo, México. Although dwarf coati is critically threatened with extinction, there are still important knowledge gaps about its biology and ecology. We are unaware of relevant published aspects of its trophic ecology and there is no information on its feeding habits. Therefore, our objective was to report, for the very first time, details on food items in the diet of the dwarf coati. Between September 2013 and December 2014, we recorded sightings of groups and solitary individuals of dwarf coati. Some of these sightings allowed us to directly record the consumption of food items, mainly fruits, which were later identified by collecting samples of the consumed material and the fruiting plant. We recorded a total of 25 sightings of dwarf coati while consuming food items. In 88 % (n = 22) of the records, we recorded the consumption of fruit from 8 species, represented by 8 families of wild plants. Additionally, we obtained records of the species consuming sea turtle eggs (n = 1) and organic waste of anthropic origin (n = 2). The evidence of the consumption of fruit and food items of different origin supports the expectation that the dwarf coati has an omnivorous diet mainly based on fruit, which coincides with that reported for other species of the same genus, the white-nosed coati (N. narica) and brown-no-sed coati (N. nasua).
Content may be subject to copyright.
THERYA NOTES 2023, Vol. 4 : 34-39 DOI: 10.12933/therya_notes-23-102 ISSN 2954-3614
First detailed record of food items in the diet of the dwarf coati
(Nasua nelsoni) of Cozumel Island, México
Primer registro detallado de alimentos en la dieta del coatí enano
(Nasua nelsoni) de Isla Cozumel, México
César r. rodríguez-Luna1, david vaLenzueLa-gaLván2*, and aLfredo d. Cuarón3
1Departamento de Ecología Humana, Centro de Investigación y de Estudios Avanzados del Instituto Politécnico Nacional Unidad
Mérida. Antigua carretera a Progreso Km 6, C. P. 97310, Mérida. Yucatán, México. E-mail: cesar.rodriguez@cinvestav.mx (CRR-L).
2Departamento de Ecología Evolutiva, Centro de Investigación en Biodiversidad y Conservación, Universidad Autónoma del Es-
tado de Morelos. Avenida Universidad 1001, C. P. 62209, Cuernavaca. Morelos, México. E-mail: dvalen@uaem.mx (DV-G).
3SACBÉ-Servicios Ambientales, Conservación Biológica y Educación A. C. Callejón del Aguacate 95, C. P. 04010, Coyoacán. Ciudad
de México, México. E-mail: cuaron@gmail.com (ADC).
*Corresponding author
The dwarf coati (Nasua nelsoni) is an endemic mammal to Cozumel Island, Quintana Roo, México. Although dwarf coati is critically threa-
tened with extinction, there are still important knowledge gaps about its biology and ecology. We are unaware of relevant published aspects
of its trophic ecology and there is no information on its feeding habits. Therefore, our objective was to report, for the very rst time, details
on food items in the diet of the dwarf coati. Between September 2013 and December 2014, we recorded sightings of groups and solitary
individuals of dwarf coati. Some of these sightings allowed us to directly record the consumption of food items, mainly fruits, which were
later identied by collecting samples of the consumed material and the fruiting plant. We recorded a total of 25 sightings of dwarf coati while
consuming food items. In 88 % (n = 22) of the records, we recorded the consumption of fruit from 8 species, represented by 8 families of wild
plants. Additionally, we obtained records of the species consuming sea turtle eggs (n = 1) and organic waste of anthropic origin (n = 2). The
evidence of the consumption of fruit and food items of dierent origin supports the expectation that the dwarf coati has an omnivorous diet
mainly based on fruit, which coincides with that reported for other species of the same genus, the white-nosed coati (N. narica) and brown-no-
sed coati (N. nasua).
Key words: Carnivore; insular endemic; pizote; procyonid; threatened species; trophic niche.
El coatí enano (Nasua nelsoni) es un mamífero endémico de Isla Cozumel, Quintana Roo, México. A pesar de que el coatí enano es una
especie críticamente amenazada con la extinción, aún existen importantes vacíos de conocimiento sobre su biología y ecología. Se descono-
cen aspectos relevantes de su ecología tróca y no existe información especíca sobre sus hábitos alimentarios. Por ello, nuestro objetivo fue
reportar, por primera vez, detalles sobre los alimentos que conforman parte de la dieta del coatí enano. Entre septiembre de 2013 y diciembre
de 2014, registramos avistamientos de grupos e individuos solitarios de coatí enano. Algunos de estos avistamientos nos permitieron registrar
directamente el consumo de alimentos, principalmente frutas, que luego fueron identicados mediante la recolección de muestras del mate-
rial consumido y de la planta madre. Registramos 25 avistamientos de individuos de coatí enano mientras consumían alimentos. En 88 % (n =
22) de esos avistamientos, registramos el consumo de frutos de 8 especies, representadas por 8 familias de plantas silvestres. Adicionalmente,
obtuvimos registros del coatí enano mientras consumía huevos de tortuga marina (n = 1) y desechos orgánicos de origen antrópico (n = 2).
La evidencia del consumo de frutas aunado al consumo de alimentos de diferente origen apoya la idea de que el coatí enano tiene una dieta
omnívora basada principalmente en el consumo de frutas, lo que coincide con información reportada para otras especies del género, como el
coatí de nariz blanca (N. narica) y el coatí sudamericano (N. nasua).
Palabras clave: Carnívoro; endémico insular; especie amenazada; nicho tróco; pizote; prociónido.
© 2023 Asociación Mexicana de Mastozoología,www.mastozoologiamexicana.org
The dwarf coati (Nasua nelsoni) is a mammalian carnivore
of the Procyonidae family, endemic to Cozumel Island,
Quintana Roo, México. It is a species classied as Endan-
gered, according to Mexican legislation (SEMARNAT 2010),
and listed in Appendix III of the Convention on Interna-
tional Trade in Endangered Species of Wild Fauna and Flora
(CITES; Valenzuela-Galván et al. 2014). In México, the spe-
cies has been considered as a priority in terms of conser-
vation among terrestrial mammals of the order Carnivora
(Valenzuela-Galván and Vázquez 2007). The dwarf coati is
an insular species similar to its continental congener, the
white-nosed coati (Nasua narica), but with signicantly
less weight, and smaller size and tooth length, compared
to the latter (Valenzuela-Galván et al. 2014). It is a species
that faces severe conservation problems related to the
introduction of exotic species, loss of natural habitat, sto-
chastic events (mainly hurricanes) and to its low popula-
tion size, which is estimated has not recovered from histor-
ical genetic bottlenecks, and hence further reduction of its
population is possible (Cuarón et al. 2004, 2009; McFadden
35 THERYA NOTES Vol. 4 :34-39
Cozumel’s dwarf coati diet
et al. 2010; Flores-Manzanero et al. 2022). Available genetic
information about the dwarf coati strongly supports that
its taxonomic position as a distinct species should be con-
sidered (something that has been recently debated; see
Valenzuela-Galván et al. 2023 and Ruiz-García et al. 2023).
Also, its status in the IUCN Red List of Threatened species
should be recognized as a Critically Endangered species,
and its population managed in accordance, or at the very
least as an Evolutionary Signicant Unit (sensu Moritz 1994;
Flores-Manzanero et al. 2022).
Despite its endemism and vulnerability, it is a species
for which little is known about its natural history, biol-
ogy, behavior, and ecological aspects. Research eorts
have focused on determining its population size (Cuarón
et al. 2004) and more recently spatio-temporal ecology
(Rodríguez-Luna 2015) and conservation genetics (Flores-
Manzanero et al. 2022). Conservation work has resulted
in the creation of an extensive system of state and federal
protected areas and the recognition of the entire Cozumel
Island and surrounding sea as a Biosphere Reserve of UNES-
CO’s Man and Biosphere Program (Cuarón et al. in press).
However, there is still an important knowledge gap about
its trophic niche. Regarding its feeding habits, it is consid-
ered that they could be similar to those of N. narica (Cuarón
et al. 2009): an omnivorous species that feeds mainly on
fruits and arthropods (Valenzuela-Galván et al. 2014). Nev-
ertheless, eldwork is still needed to demonstrate this.
Knowledge about the feeding habits of animals helps
to understand ecological niche relationships, since they
play an important role in segregation, competition, coex-
istence (Schoener 1974), population dynamics (Taper and
Marquet 199), habitat use and even the social organiza-
tion of a species (Mills 1992; ; Manfredi et al. 2004; Casella
and Cáceres 2006). Besides, it is valuable information to
support conservation actions. Therefore, our objective in
this work was to report the very rst records of food items
ingested by the dwarf coati of Cozumel Island, obtained
through direct observation.
The study area was Cozumel Island, Quintana Roo,
México (Figure 1). It is an oceanic island located in the Mexi-
can Caribbean Sea with ca. 478 km2 and extreme coordinates
20° 16' 18.2” – 20° 35' 32.28” N and 86° 43' 23.3” – 87° 01' 31.1”
W (Cuarón 2009). The vegetation on the island consists of a
well-dened gradient that begins from the eastern coastal
strip with coastal dune vegetation followed by areas of
tasistal (Acoelorhaphe wrightii), mangrove (Rhizophora man-
gle, Laguncularia racemosa), tropical dry forest and medium
sub-deciduous forest in the central portion of the island,
which is the predominant vegetation type (Téllez et al. 1989;
Figure 1). Climate type is AmW(I), warm humid with abun-
dant rains in summer; average annual temperature is 27.5 °C
and average annual precipitation is 1,403 mm (INEGI 2016).
Between September 2013 and December 2014 in Cozu-
mel Island, we carried out a study on the spatial ecology of
the dwarf coati for which it was necessary to capture and
radio tag several individuals of the species (Rodríguez-Luna
2015). During the development of the eldwork to obtain
radiotracking locations, we recorded sightings of groups
and solitary individuals of the species at dierent places on
the island. For some of the sightings we observed individu-
als of dwarf coati foraging and even consuming food items.
For each of these sightings, we recorded the geolocation,
vegetation type, and, when possible, we took photographic
evidence with a portable camera (NikonTM mod. P100).
When we recorded an observation of the consumption of
fruits, we collected samples of them as well as of the fruit-
ing plant for the subsequent identication of the species.
For plant identication, we used the Catalogo de Flora de la
Península de Yucatán of the Centro de Investigación Cientí-
ca de Yucatá A. C. (https://www.cicy.mx/sitios/ora%20
digital/index.php), as well as reference material with special-
ized support from personnel of the Laboratorio de Ecología
de Plantas from the Cozumel campus of the Universidad
Autónoma de Quintana Roo.
We obtained a total of 25 georeferenced sightings of
dwarf coati where we observed the consumption of food
items by the species (Figure 1). Most of the sightings (56%;
n = 14) occurred in areas covered by tropical medium sub-
deciduous forest, 32 % (n = 8) occurred in coastal dune
areas, 8 % (n = 2) in secondary vegetation and one sighting
(4 %) occurred on a beach in the east coast with no appar-
ent vegetation (Table 1).
Figure 1. Study area in Cozumel Island, Quintana Roo, México, and spatial locations of
the sighting points (red dots) where we recorded the food intake by the dwarf coati (Nasua
nelsoni). In the gure we show the town of San Miguel de Cozumel (black triangle) and the
land cover according to freely available information on Land Use and Vegetation (sVII) from
the Instituto Nacional de Estadística y Geografía (INEGI), available at https://www.inegi.org.
mx/temas/usosuelo/#Descargas. Land cover is described as: Aq, aquatic vegetation; CD,
coastal dune; DoV, area devoid of vegetation; G, grasslands; HS, human settlements; M,
mangroves; TMSF, tropical medium sub-deciduous forest; WB, water bodies.
www.mastozoologiamexicana.org 36
Rodríguez-Luna et al.
We were able to identify the consumption of fruits (Fig-
ure 2) of 8 wild plant species, represented by 8 genera, 8
families and 7 orders (Table 1): Xylopia frutescens Aubl., Byr-
sonima bucidifolia Standl., Cordia sebestena L., Coccoloba
uvifera (L.) L., Diospyros salicifolia Humb. & Bonpl. ex Willd.,
Cascabela gaumeri (Hemsl.) Lippold, Scaevola plumieri (L.)
Vahl and Jacquinia arborea Vahl.
In addition, we recorded 1 sighting in which a dwarf coati
consumed sea turtle eggs (most probably of Chelonia mydas,
since the majority of nests at Cozumel are from this species)
on an open beach and 2 sightings of the species consuming
organic food waste of anthropic origin (Figure 3).
Our records of dwarf coati consuming fruits, sea turtle
eggs and organic waste of anthropic origin, represents the
rst report of food items identied in detail in the species
diet. Other species of the genus Nasua have a high con-
sumption of fruits (Gompper 1995; Gompper and Decker
1998). The white-nosed coati (N. narica) consumes predom-
inantly fruits, but also invertebrates and small vertebrates
in variable proportions, both in the northernmost part of
Figure 2. Photographic records of dwarf coati of Cozumel Island (Nasua nelsoni), prior to the consumption of fruits (marked in red circles) of species a) Xylopia frutescens and b)
Diospyros yucatanensis.
37 THERYA NOTES Vol. 4 :34-39
Cozumel’s dwarf coati diet
its distribution in the United States of America (Wallmo
and Galliziolli 1954; Kaufmann et al. 1976), México (Delibes
et al. 1989; Valenzuela-Galván 1998; Valenzuela-Galván et
al. 2014) and in the southernmost part of its distribution
in Central America (Kaufmann 1962; Smythe 1970; Gomp-
per 1995, 1996). On the other hand, the brown-nosed
coati (N. nasua) also feeds mainly on fruit and consumes a
variable proportion of invertebrates in its diet (Gompper
and Decker 1998; Alves-Costa et al. 2004; Alves-Costa and
Eterovick 2007; Hirsch 2009; Aguiar et al. 2011; Bianchi et al.
2013; Ferreira et al. 2013).
Among the 8 species that we report in the diet of the
dwarf coati, fruits from 5 families have a previous record
of consumption in Nasua spp.: Polygonaceae, Ebena-
ceae, Primulaceae, Malpighiaceae and Annonaceae (Rus-
sell 1982; Valenzuela-Galván 1998; Hirsch 2009; Bianchi
et al. 2013), but for 3 species and plant families, our study
reports for the rst time their consumption by a species
in the genus Nasua (Table 1). We also recorded the con-
sumption of sea turtle eggs in the northern part of the east
coast of Cozumel Island. Nest predation is well known by
people who are related to sea turtle (i.e., Chelonia mydas,
Caretta caretta, Eretmochelys imbricata) conservation work
on the island; however, there are no previous published
data on nest predation in the study area by the dwarf coati,
although consumption of sea turtle eggs by N. narica has
been reported for dierent zones across its geographical
distribution (Fowler 1979; Valenzuela-Galván 1998; García
et al. 2003; Ruthig 2019). Finally, we recorded individuals
of dwarf coati feeding on organic waste of anthropic ori-
gin inside garbage containers in the southern portion of
the island (Figure 3), although we were unable to identify
the elements ingested. Coati's omnivorous diet allows it
to obtain food supplementation in urban environments,
where they frequently feed on organic waste of anthropic
origin (Alves-Costa et al. 2004; Hirsch 2009); this represents
one of the factors that can favor the establishment of the
species and even the maintenance of stable population
density over time in urban areas (Barreto et al. 2021).
Thus, with our records of the consumption of fruits, sea
turtle eggs, and organic waste of anthropic origin, the idea
that the dwarf coati has an omnivorous diet based mainly
on fruit consumption is reinforced. This fact coincides with
information reported for other species of the genus Nasua.
However, the detailed study of the feeding habits of the
species must be deepened to contribute to the knowledge
of its basic ecology and sustain conservation actions for this
critically endangered endemic species.
Acknowledgements
We thank two anonymous reviewers for useful suggestions
to previous versions. We acknowledge the help received
from the following local institutions: Fundación de Parques
y Museos de Cozumel, Ayuntamiento de Cozumel and
Comisión de Agua Potable y Alcantarillado. A. Collantes
Table 1. Records of food items consumed by the dwarf coati (Nasua nelsoni) of Cozumel Island, México by vegetation type. * Indicates this is the rst time this species and plant
family is reported to be consumed by a species in the genus Nasua. Vegetation types are designated as follows: CD, coastal dune; DoV, area devoid of vegetation; TMSF, tropical medium
sub-deciduous forest; SV, secondary vegetation.
Food type Order Family Species
Number of
records
Percentage of
records
Vegetation
type
Fruits Asterales Goodeniaceae* Scaevola plumieri* 1 4 CD
Boraginales Boraginaceae* Cordia sebestena* 2 8 CD
Caryophyllales Polygonaceae Coccoloba uvifera 2 8 CD
Ericales Ebenaceae Diospyros salicifolia 2 8 TMSF
Primulaceae Jacquinia arborea 1 4 CD
Gentianales Apocynaceae* Cascabela gaumeri* 2 8 CD
Magnoliales Malpighiaceae Byrsonima bucidifolia 4 16 TMSF
Malpighiales Annonaceae Xylopia frutescens 8 32 TMSF
Sea turtle eggs - - - 1 4 DoV
Anthropic waste - - - 2 8 SV
Total 25 100 4
Figure 3. Photographic record of dwarf coati of Cozumel Island (Nasua nelsoni),
prior to the consumption of organic waste of anthropic origin in the southern part of
the island.
www.mastozoologiamexicana.org 38
Rodríguez-Luna et al.
and O. Yam (UQROO) provided valuable help for ecological
sampling of vegetation. Partial funding for this research
was provided by CONABIO (project LI028 assigned to the
last author), by Idea Wild (funds provided to the rst author)
and by the program PROCER-2013- CONANP through a
project assigned to M. Á. Martínez Morales (ECOSUR). The
rst author received funding from CONACyT through schol-
arships 361457 and MZO2015. Individuals were captured
under the permit SGPA/DGVS/00529/14 assigned to the
second author. We also thank the Maestría en Biología Inte-
grativa de la Biodiversidad y la Conservación (CIByC-UAEM).
Literature cited
aguiar, L. M., et al. 2011. Diet of brown-nosed coatis and crab-
eating raccoons from a mosaic landscape with exotic planta-
tions in southern Brazil. Studies on Neotropical Fauna and
Environment 46:153-161.
aLves-Costa, C. P., g. a. da fonseCa, and C. Christófaro. 2004. Vari-
ation in the diet of the brown-nosed coati (Nasua nasua) in
southeastern Brazil. Journal of Mammalogy 85:478-482.
aLves-Costa, C. P., and P. C. eteroviCk. 2007. Seed dispersal ser-
vices by coatis (Nasua nasua, Procyonidae) and their redun-
dancy with other frugivores in southeastern Brazil. Acta
Oecologica 32:77-92.
Barreto, W. t. g., et al. 2021. Density and survivorship of the
south American coati (Nasua nasua) in urban areas in cen-
tral–Western Brazil. Hystrix Italian Journal of Mammalogy
32:82-88.
BianChi, r., et al. 2013. Intraspecic, interspecic, and seasonal
dierences in the diet of three mid-sized carnivores in a large
Neotropical wetland. Acta Theriologica 59:13-23.
CaseLLa, J., and n. C. CáCeres. 2006. Diet of four small mammal
species from Atlantic Forest patches in South Brazil. Neo-
tropical Biology and Conservation 1:5-11.
Cuarón, a. d. 2009. Cozumel. Pp. 203-206 in Encyclopedia of
Islands (Gillespie, R., and D. A. Clague, eds.). University of Cali-
fornia Press. Berkeley, U.S.A.
Cuarón, a. d., et al. 2004. The status of dwarf carnivores on Cozu-
mel Island, Mexico. Biodiversity and Conservation 13:317-331.
Cuarón, a. d., et al. 2009. Conservation of the endemic dwarf
carnivores of Cozumel Island, Mexico. Small Carnivore Con-
servation 41:15-21.
Cuarón, a. d., et al. (in press). Isla Cozumel: biodiversidad,
conservación y desarrollo sustentable. In La Ciencia que
Necesitamos para el Océano que México Quiere: la Década
del Océano 2021-2030 (Rivera Arriaga, E., and I. Azuz Adeath,
coords.). Universidad Autónoma de Campeche. México City,
México.
deLiBes, M., L. hernández, and f. hiraLdo. 1989. Comparative food
habits of three carnivores in western Sierra Madre, Mexico.
Zeitschrift für Säugetierkunde 54:107-110.
ferreira, g. a., et al. 2013. Diet of the coati Nasua nasua (Car-
nivora: Procyonidae) in an area of woodland inserted in an
urban environment in Brazil. Revista Chilena de Historia Nat-
ural 86:95-102.
fLores-Manzanero, a., et al. 2022. Conservation genetics of two
critically endangered island dwarf carnivores. Conservation
Genetics 23:35-49.
foWLer, L. e. 1979. Hatching success and nest predation in the
green sea turtle, Chelonia mydas, at Tortuguero, Costa Rica.
Ecology 60:946-955.
garCía, a., g. CeBaLLos, and r. adaya. 2003. Intensive beach man-
agement as an improved sea turtle conservation strategy in
Mexico. Biological Conservation 111:253-261.
goMPPer, M. e. 1995. Nasua narica. Mammalian Species
487:1-10.
goMPPer, M. e. 1996. Sociality and asociality in white-nosed
coatis (Nasua narica): foraging costs and benets. Behavioral
Ecology 7:254-263.
goMPPer, M. e., and d. M. deCker. 1998. Nasua nasua. Mamma-
lian Species 580:1-9.
hirsCh, B. t. 2009. Seasonal variation in the diet of ring-tailed
coatis (Nasua nasua) in Iguazu, Argentina. Journal of Mam-
malogy 90:136-143.
instituto naCionaL de estadístiCa y geografía (inegi). 2016. Anuario
estadístico y geográco de Quintana Roo. Instituto Nacional
de Estadística y Geografía. Aguascalientes, México.
kaufMann, J. h. 1962. Ecology and social behavior of the coati,
Nasua narica, on Barro Colorado Island, Panama. University
of California Publications in Zoology 60:95-222.
kaufMann, J. h., d. C. Lanning, and s. e. PooLe. 1976. Current status
and distribution of the coati in the United States. Journal of
Mammalogy 57:621-637.
Manfredi, C., et al. 2004. Geographical variation in the diet of
Georoy's cat (Oncifelis georoyi) in Pampas grassland of Ar-
gentina. Journal of Mammalogy 85:1111-1115.
MCfadden, k. W., et al. 2010. Vulnerable island carnivores: the
endangered endemic dwarf procyonids from Cozumel Is-
land. Biodiversity and Conservation 19:491-502.
MiLLs, M. g. L. 1992. A comparison of methods used to study
food habits of large African carnivores. Pp. 1112-1124 in
Wildlife 2001: populations (McCullough, D. R., and R. H. Bar-
rett, eds.). Springer Science and Business Media. Dordrecht,
Netherlands.
Moritz, C. 1994. Dening evolutionary signicant units. Trends
in Ecology and Evolution 9:373-375.
rodríguez-Luna, C. r. 2015. Determinación del ámbito hoga-
reño, uso de hábitat y patrones de actividad del tejón enano
(Nasua nelsoni) de la isla de Cozumel, Quintana Roo, México.
Tesis de Maestría. Maestría en Biología Integrativa de la Bio-
diversidad y la Conservación. Centro de Investigación en
Biodiversidad y Conservación-Universidad Autónoma del Es-
tado de Morelos. Morelos, México.
ruiz-garCía, M., et al. 2023. Response to Valenzuela-Galván et
al. 2023: It is not necessary to “create” a new species for the
sake of conservation: the case of the Cozumel’s coati. Therya
14:201-206.
russeLL, J. k. 1982. Timing of reproduction by coatis (Nasua
narica) in relation to uctuations in food resources. Pp.
413–431 in The ecology of a tropical forest: seasonal rhythms
and long-term changes (Leigh, E. G. Jr., A. S. Rand, and D. M.
Windsor, eds.). Smithsonian Institute Press. Washington D.
C., U.S.A.
ruthig, g. r. 2019. Aggregations of olive ridley sea turtle (Lepi-
dochelys olivacea Eschscholtz, 1829) nests leads to increased
human predation during an arribada event. Herpetology
Notes 12:1-7.
39 THERYA NOTES Vol. 4 :34-39
Cozumel’s dwarf coati diet
seCretaría de Medio aMBiente y reCursos naturaLes (seMarnat).
2010. Norma Ocial Mexicana NOM-059-SEMARNAT-2010,
Protección ambiental-Especies nativas de México de ora y
fauna silvestres-Categorías de riesgo y especicaciones para
su inclusión, exclusión o cambio-Lista de especies en riesgo.
Secretaría del Medio Ambiente y Recursos Naturales. México
City, México.
sChoener, t. W. 1974. Resource partitioning in ecological com-
munities. Science 185:27-39.
sMythe, n. 1970. The adaptive value of the social organiza-
tion of the coati (Nasua narica). Journal of Mammalogy
51:818-820.
taPer, M. L., and P. a. Marquet. 1996. How do species really di-
vide resources? The American Naturalist 147:1072-1086.
téLLez, o., et al. 1989. Las plantas de Cozumel (guía botánico-
turística de la Isla de Cozumel, Quintana Roo). Instituto de Bi-
ología, Universidad Nacional Autónoma de México. México
City, México.
vaLenzueLa-gaLván, d. 1998. Natural history of the White-nosed
coati, Nasua narica, in a tropical dry forest of western Mexico.
Revista Mexicana de Mastozoología (Nueva época) 3:26-44.
vaLenzueLa-gaLván, d., et al. 2014. Nasua nelsoni. Pp. 569–571 in
Mammals of Mexico (Ceballos, G., ed.). John Hopkins Univer-
sity Press. Maryland, U.S.A.
vaLenzueLa-gaLván, d., et al. 2023. A single sample is not enough
to claim systematic conclusions, much less for taxa of con-
servation concern: comments on Jaramillo and Ruiz- García
(2022). Therya 14:197-199.
vaLenzueLa-gaLván, d., and L. B. vázquez. 2007. Consideraciones
para priorizar la conservación de los carnívoros mexicanos.
Pp. 197-214 in Tópicos en sistemática, biogeografía, ecología,
y conservación de mamíferos (Sánchez-Rojas, G., and A. E.
Rojas-Martínez, eds.). Universidad Autónoma del Estado de
Hidalgo. Hidalgo, México.
WaLLMo, o. C., and s. gaLLizioLi. 1954. Status of the coati in Ari-
zona. Journal of Mammalogy 35:48-54.
Associated editor: José F. Moreira Ramírez.
Submitted: February 16, 2023; Reviewed: April 10, 2023.
Accepted: April 20, 2023; Published on line: May 8, 2023.
... We consider that this could be explained by the fact that dog presence is linked to human activity (Bautista 2006), which is also related to greater food availability for the native carnivores (particularly anthropogenic food waste), making them more prone to stay in a site despite the presence of dogs. In fact, it has been reported that the diet of both native carnivores can include anthropogenic food, although in a small percentage (Rodríguez-Luna et al. 2023;. Furthermore, at certain sites on the island, local residents and tourists have been reported to directly feed individuals of both native carnivore species (Rodríguez-Luna 2015;Lara-Godínez 2018). ...
... Although the Cozumel raccoon is considered omnivorous, its diet is mainly based on crabs (>50% of the diet; McFadden et al. 2006;, which are abundant in mangroves and coastal dune vegetation, where the probability of Cozumel raccoon occupancy was the highest. The available information on the diet of the dwarf coati (Rodríguez-Luna 2015; Rodríguez-Luna et al. 2023) indicates that it is based mainly on fruits, and it is also expected to have a diet similar to that of the continental coati which is composed mainly of fruit and leaf litter arthropods, and a lower and a more variable percentage of vertebrates (Valenzuela 1998;Valenzuela-Galván et al. 2014). In the case of the opossum, there is no information on its diet on Cozumel, and relatively little information for other sites in Mexico. ...
Article
Species face increasing threats from anthropogenic disturbances to natural habitats, and we need to understand how threatened species are affected. For example, studying animals’ behavior and responses toward co-occurring species provides information on ecological interactions. We explored the patterns and drivers of the spatial use of two native carnivores endemic to Cozumel Island, Mexico, the Cozumel raccoon (Critically Endangered) and the dwarf coati (considered as Threatened in Mexico). We used multi-seasonal occupancy models to assess the effect that environmental variables, or the interactions with the other endemic carnivore, with a potentially competing species (common opossum) and with an invasive predator (dog), have on the activity of each endemic carnivore. We also compared their daily activity patterns. Habitat type was the main factor driving the detection and occupancy probability of both native carnivores that showed low to moderate overlap in daily activity patterns with competing species and with an invasive predator. Neither habitat disturbance nor dogs affected carnivore occupancy, suggesting that both variables have not reached a critical threshold to negatively influence the occurrence of native carnivores. Our results are relevant for understanding the spatiotemporal ecological requirements and constraints of two endangered endemic carnivores and for planning actions for their conservation.
Preprint
Full-text available
Given the growing anthropogenic disturbances of habitats, species are facing several threats and this makes it very important to know the impact of these disturbances on the presence of species. Our objective was to understand the patterns and drivers of the spatial use of the pygmy raccoon Procyon pygmaeus , a carnivore endemic to Cozumel Island and considered critically endangered with extinction. Considering that the loss and fragmentation of natural habitats in Cozumel has increased in recent decades and with this, a greater presence of feral dogs on inland areas of the island has also been evident, we used multi-seasonal single-species occupancy models to assess the effect of two variables on pygmy raccoon activity: a) the type and degree of habitat disturbance and b) the interactions between potentially competing and also endemic species (dwarf coati Nasua nelsoni and common opossum Didelphis virginiana cozumelae ) and an invasive predator (feral dog, Canis lupus familiaris ). Additionally, we compare the temporal patterns of the activity of the studied species. We found a difference in the probability of detection of the pygmy raccoon throughout the years, and the type of habitat was driving the probability of occupancy of the pygmy raccoon. The overlap between the temporal activity patterns of the pygmy raccoon and the competing species was high, while it was low with that of the invasive predator, the dog, which showed a pattern almost entirely diurnal. We found that habitat disturbance or the presence of dogs on the island has not yet reached a sufficient threshold to negatively impact the spatial use patterns of the pygmy raccoon. but we consider that these scenarios might change dramatically if disturbance or the presence of dogs increases in habitats with a higher presence of pygmy raccoon. Our results have relevant implications for understanding its ecological requirements and limitations and for planning actions for its conservation.
Article
Full-text available
Genetic diversity is crucial for conservation biology and for understanding evolutionary processes. Oceanic islands harbor a unique biota and high endemism, with populations frequently facing detrimental genetic processes (e.g. drift, bottlenecks). Human activities like habitat transformation further increase extinction risk of insular biota. Mammals comprise the most endangered group among insular fauna. Our aim was to evaluate the genetic and evolutionary patterns of two critically endangered dwarf carnivores from Cozumel Island, the pygmy raccoon (Procyon pygmaeus) and the dwarf coati (Nasua nelsoni), at both historical and contemporary evolutionary scales. We also reviewed their genetic relationships with their mainland counterparts (P. lotor, N. narica), not intended to describe their phylogeny but to ascertain their endemism. Our mitochondrial results support that both Cozumel carnivores are divergent from continental populations, strengthening their endemic status. Both species showed moderate levels of nuclear genetic diversity that were, as expected for island populations, lower in comparison with their mainland congeneric species; they also exhibited significantly low population sizes. We documented historical and contemporary bottleneck signals for P. pygmaeus, whereas N. nelsoni may be suffering the initial stages of a bottleneck not yet fully manifested. The pygmy raccoon is structured into two isolated genetic clusters likely due to interactions with humans on the north of the island, where most potential for disease transmission and health problems exist. We also add evidence about the introduction of the mainland species into the island, risking genetic introgression and hybridization. We discuss specific conservation measures that should include our genetic information, directed to the long-term viability of these endemic carnivores.
Article
Full-text available
Coatis are omnivores whose diet consists of small vertebrates, invertebrates, and fruit. In urban areas, they may ingest food waste that has been discarded in deposits near their habitat, or they may consume food offered by humans. The present work investigates the diet of coatis through analysis of 56 fecal samples collected from Morro Imperador, a fragment of woodland inserted into an urban center in the municipality of Juiz de Fora, State of Minas Gerais, Brazil. The results point to a diet with niche breadth of 0.4 in which the percentage of occurrence of insects (34.9 %) and fruit (19.9 %) comprise the main dietar y items. The presence of food due to human action (direct or indirect) is also constant throughout the year (14.1 %), thereby demonstrating the ability of these animals to adapt to modifi ed environments.
Article
Full-text available
We described the diets of two procyonids, the brown-nosed coati Nasua nasua and the crab-eating raccoon Procyon cancrivorus, through analysis of stomach contents of road-killed specimens in southern Brazil. We compared them with previously published dietary information for another syntopic mesopredator, the crab-eating fox Cerdocyon thous. The landscape of the study area includes native grasslands, forests, exotic tree plantations, and other crops. Food items were represented by frequency of occurrence (FO) and relative volume (RV). Stomach contents of 23 coatis were analyzed. Animal and plant items were equally frequent, although the volume of plants was greater. Exotic plant species were consumed more than native plants. Among prey items, invertebrates were more important than vertebrates, mainly because of the frequency of coleopterans and annelids and the volume of necrophagous dipteran larvae. Five specimens of raccoons were analyzed, in which animal items had the highest FO and plant items had the highest RV. Both invertebrate and vertebrate prey had the same FO, although vertebrates had a higher RV. Our data suggest that these procyonids are opportunistic hypocarnivores, utilizing anthropic sources, with diet overlap. The coatis also overlapped their diet substantially with the foxes. The stomach-contents analysis revealed the importance of fruit pulp biomass, soft-bodied animals such as larvae, and also soil, which might indicate feeding habits such as scavenging and geophagy.
Article
We determined the diet of the brown-nosed coati (Nasua nasua) in an urban semideciduous forest fragment in southeastern Brazil. Coati feces were collected weekly for 3 years. The 226 fecal samples included plant parts (85.4%), insects (75.7%), millipedes (53.9%), fruits (48.7%), spiders (33.6%), organic waste (9.7%), vertebrates (9.3%), and gastropods (2.6%). More spiders and millipedes were consumed during the wet season, and more fruits were consumed in the dry season. The consumption of vertebrates, fruits, and millipedes differed among different years. The monthly consumption of spiders and millipedes was positively correlated with rainfall. The consumption of fruits was negatively correlated with the consumption of millipedes and insects. Fruits were an important resource during periods of arthropod scarcity. Coatis ingested and defecated intact seeds of 49 plant species, indicating that they can be important seed dispersers. The consumption of vertebrates was occasional and varied.
Chapter
Five methods for studying food habits of large African carnivores are evaluated. Fecal analysis is useful for a basic description of the diet, provided that an adequate sample of scats can be obtained. However, it is impossible to quantify the amount eaten and to determine the proportions of killed versus scavenged food. Tracking spoor in restricted habitats is useful for most species, except the brown hyena (Hyaena brunnea). Opportunistic, and for most species, radio-location observations are biased towards large prey animals, because small animals are eaten quickly, leaving no trace. However, the data can be used to study sex and age selection of adult prey. Direct observations provide accurate measurements of consumption rates, killing frequency, and prey selection, provided they can be carried out without disturbing predator or prey. Mixing data from incompatible techniques must be avoided.
Article
Green turtle hatching success and nest predation were investigated at Tortuguero, Costa Rica, during July-November 1977. Forty-two percent of 350 study area nests and 57% of 237 beach survey nests produced emerging young; 38% and 24%, respectively, were destroyed by dogs, coatis, and vultures. The mean emergence percentage for the successful study area nests was 83%. About 13% of all eggs deposited did not hatch. A mean incubation period of 62 d and a mean clutch size of 104 eggs were recorded. Emergence success was not influenced by other recorded parameters (nest position on beach, rainfall, turtle's tag year, time of season, incubation period, and clutch size). Incubation period was related to nest position and clutch size. Dogs, coatis, and black and turkey vultures were the chief predators at Tortuguero; dogs did the most damage. Dogs and coatis found nests at all stages of development, but destroyed more nests containing hatchlings than nests containing unhatched eggs. Predation was related to nest position, but not to nest density. Nests were destroyed in equal proportion on the entire 35.4 km of beach. Predator activity was not consistent throughout the season; proportionally more nests were destroyed near the end of the nesting season than during the beginning.
Article
Coatis have been in the montane border country of southeastern Arizona and southwestern New Mexico for more than 80 years. Their numbers and range in the United States have fluctuated. The highest known population occurred in the late 1950's, followed by a precipitous decline caused apparently by canine distemper or a similar disease. Since that time there has been a slow, irregular recovery. The biology of coatis in the U.S. is similar to that described previously in Panama, but with important differences in the much drier and cooler habitat. Coatis are opportunistic omnivores in all habitats, eating whatever fruits, invertebrates, and small vertebrates are easily obtained. Females and immature males live in bands whereas the adult males are usually solitary, but at the northern margin of the species' range, adult males may more often accompany bands. Coatis in the U.S. have relatively large home ranges and may be semi-nomadic. They have been seen most commonly at elevations of 1400 to 2000 meters. Coatis are preeminently woodland and forest inhabitants, and their distribution in the U.S. coincides almost exactly with that of the Madrean Evergreen Woodland which extends into the mountains of southern Arizona and New Mexico from the Sierra Madre of Mexico. Coatis breed from the Animas Mountains in southwestern New Mexico west to the Baboquivari Mountains in Arizona, and north as far as the Gila River. Marginal records from north of the Gila are from occasional wanderers or released captives. There is no evidence that coatis in the U.S. are currently expanding their breeding range or approaching the population levels of the late 1950's. Their numbers and spread are limited by some combination of aridity, cold, disease, and unsuitable plant cover and food resources. Discovering the coatis' role in the natural environment of the southwestern U.S. will require the combined efforts of many people; the Coati Study Project has been formed to coordinate these studies.
Article
We show that the relationship between variance in population energy use and variance in species abundance depends critically on the model of causal relationships among metabolic rate, body size, and population density assumed, provided that they specify alternative paths of error propagation. It has been claimed that the allometric relationship between population density and body size indicates that species within communities use resources less equitably than would be inferred from a particular species abundance distribution. Our analysis of 41 local bird communities shows that this claim is supported only if it is assumed that both body size and metabolic rate are a consequence of population density. A more realistic model that assumes a causal role for body size as affecting metabolic rate and population density provides estimates of variance in population energy use that closely match the pattern of variance in population density. This implies that the apportionment of individuals and resources, among species, are equivalent processes.