| Important synonyms: Caiman crocodilus yacare
Common names: Yacaré, Jacaré, Lagarto, Yacaré negro, Yacaré tinga Range: Argentina, Brazil, Bolivia, Paraguay Revised by Eduardo Espinosa |
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CITES: Appendix II
CSG Action Plan:
Availability of Survey Data – Adequate
Need for Wild Population Recovery – Moderate
Potential for Sustainable Management – Highest
1996 IUCN Red List: Not Listed (LRlc Lower Risk, least
concern. Widespread and numerous populations,
although locally depleted.)
Principal threats: Illegal hunting, habitat destruction.
Ecology and natural history
The yacaré caiman is found in southern Brazil and
Bolivia, southwards through the Paraguay/Paraná River
systems and into northern Argentina. Morphologically
and ecologically this species is very similar to the
common caiman, and similarly can be found in a wide
spectrum of habitat types. Most of the ecological studies
on this species have been carried out in the Pantanal
region of southern Brazil (Crawshaw and Schaller 1980,
Schaller and Crawshaw 1982, Cintra 1986). More recent
studies also include Bolivia (Pacheco 1993a, Godshalk
1994). Nesting habitats were monitored during the
incubation and hatching period (Borges and Filho 1993),
and the effect of water level on hatchlings survivorship
have also been evaluated (Continho 1993). Aerial surveys
of caiman nests have been started in the Pantanal
(Mourao et al. 1994).
Although often considered a subspecies of Caiman crocodilus, the yacaré occupies a distinct geographic range and a special position in the international skin trade and is therefore treated separately here for convenience. Resolution of the systematic relationships within the very widespread Caiman crocodilus complex is needed. Extensive surveys and specimen collection in southern Brazil, northern Bolivia and Paraguay suggest a very complex gradient of morphological features between C. crocodilus and the yacaré. Analyses of mitochondrial DNA to resolve the relationships between these taxa are incomplete and inconclusive (Brazaitis et al. 1993).
Yacaré caiman are mound nesters, with egg-laying
usually peaking in the middle wet season. Clutch size is
typically in the 25–35 range. The natural tendency of
females to guard their nests is apparently influenced by
human hunting pressure (Crawshaw 1987), which results
in decreased nest attendance and a lower hatching
success. Detailed information is now available on the
ecology of the species in the Brazilian Pantanal from the
work of Campos, Mourao and colleagues (Campos
1993, Mourao et al. 1994, Campos and Magnusson
1995, Campos et al. 1995, Mourao et al. 1996, Santos
et al. 1996, Couthino and Campos 1996).
Conservation and status
Most of what is written about the conservation of the
common caiman applies equally well to this species.
Basic survey information is available for this species in
all countries where it occurs. This information has
resulted principally from a series of CITES sponsored
surveys of southern Brazil, Bolivia, and Paraguay.
Populations of yacaré caiman are considered to be
somewhat depleted in all four countries where it occurs,
and this is principally due to widespread illegal hunting
during the 1970s and 1980s. Poaching remains a
problem throughout much of this species’ range,
particularly in Brazil (Brazaitis et al. 1988, Brazaitis
1989). However, due to their small size at maturity,
their ability to adapt to a wide variety of habitat types,
and their learned wariness, caiman are particularly
resilient to hunting pressure. Recent analyses in Brazil
suggest that the hunting pressure, while illegal, has not
negatively impacted populations and may be sustainable
(Mourao et al. 1996). Surveys in Paraguay (Scott et al.
1990, King, Aquino, Scott and Palacios 1994) and
Argentina (Waller and Micucci 1993) indicate that
extensive populations remain or have recovered from
previous exploitation since the closure of uncontrolled
exploitation and implementation of export controls.
Commercially oriented management programs are
in place in three of the four countries for yacaré.
Paraguay is moving toward sustainable management
(King, Aquino, Scott and Palacios 1994) and permitted
an experimental export quota of 5,000 in 1994. Cropping
was permitted in Bolivia, where hides were exported
under a CITES quota until a ban was instituted in 1989.
Recently, new surveys were initiated and a controlled
hunting program similar to the Venezuelan program
has been proposed (Godshalk 1994). In Brazil, hunting of
wild animals is not permitted, but ranching and farming
programs are developing rapidly. Captive breeding
farms have proliferated and Brazilian regulations
require that all caiman skins must be produced on
farms, be tagged, semiprocessed to the ‘wet blue’ stage
and have a minimum belly width of 18cm (TRAFFIC
1994). An experimental ranching system is being
developed in the Pantanal. In Argentina, a plan for the
captive rearing of yacaré for reintroduction is still
underway, which hopefully may be as successful as
the program for Caiman latirostris (Larriera 1993).
Studies on distribution, habitat characterization and
habitat availability of yacaré have been already
conducted in the province of Corrientes (Waller and
Micucci 1993). A second phase of studies is required to
define management alternatives for yacaré in this region
of Argentina.
Priority projects
High priority
Implementation of management programs in Brazil: Brazil has undertaken a very rapid development of captive breeding (farming) of caiman similar to that in Colombia. A number of facilities are registered with the government and CITES as captive breeding facilities and are producing skins for export. Unfortunately little conservation benefit is resulting from these activities. There is a need to develop government regulatory and management capacity and provide a linkage to protection of wild caiman populations and their habitats.
Control of illegal trade in Caiman yacare skins: This project
is as described in this volume for Caiman crocodilus.
Study of Caiman systematics: To clarify the complex taxonomic situation of yacaré, molecular techniques employing the D-loop of the control region of the mitochondrial DNA could be used to determine genetic relationships among subspecies because of its higher resolution (Avise 1994). The use of this region allows more accurate differentiation at a lower taxonomic level (species or subspecies rather than families) than other studies to date. Parallel studies of morphological variation, particularly in areas of intergradation are also needed.
Moderate priority
Long-term ecological studies in the Pantanal, Brazil: Like the llanos of Venezuela and Colombia, the Pantanal is a large seasonally inundated savanna that offers excellent research opportunities for the study of caiman population dynamics. The interest in the development of sustainable management programs should foster the development of research programs to investigate aspects of the life history of the yacaré.
Implementation of management program in Paraguay: A survey conducted by King, Aquino, Scott and Palacios. (1994) encountered numerous populations of yacaré. That report’s recommendations provide the basis for a sustainable utilization program for the species. At the beginning the hunting activity should be restricted to the Alto Paraguay. A continuous monitoring program to evaluate the status of the population, particularly under exploitation, will be also important to ensure the sustainability of the program.

Yacaré, Caiman yacare. This widespread species remains abundant
in the Pantanal of Brazil.
Photo by R. S. Funk.