First Observations of Nesting by the Argentine Black and
White Tegu, Tupinambis merianae, in South Florida
Tony Pernas, Dennis J. Giardina, Alan McKinley, Aaron Parns, and Frank J. Mazzotti
Southeastern Naturalist, Volume 11, Issue 4 (2012): 765–770
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2012 SOUTHEASTERN NATURALIST 11(4):765–770
First Observations of Nesting by the Argentine Black and
White Tegu, Tupinambis merianae, in South Florida
Tony Pernas1, Dennis J. Giardina2, Alan McKinley1, Aaron Parns1,
and Frank J. Mazzotti3,*
Abstract - Florida has the most species of introduced and established reptiles in the
world. There are more species of non-native lizards reproducing in Florida than native
species. Tupinambis merianae (Argentine Black and White Tegu) is established in parts
of Hillsborough and Polk counties, FL. No evidence of reproduction has been published
in other areas of Florida, although this species has been sighted in various other Florida
locations, especially in southeastern sites. Using radio-telemetry, we tracked an adult
female tegu in Miami-Dade County to a ruderal thicket with a suspected nest mound.
Upon excavation of the mound, we found one clutch of 21 eggs from the current year,
and one clutch of 22 hatched egg shells and 13 unhatched eggs from a past year. This is
the first evidence confirming expansion of a reproducing population of Argentine Black
and White Tegus into southeastern Florida. If this population is small and localized, there
is potential for removal if swift, decisive action is taken.
Non-native invasive species are a major threat to ecological integrity and
biological diversity (Parker et al. 1999, Wilcove et al. 1998). Increasing attention
is being paid to non-native amphibians and reptiles (Bomford et al. 2009,
Kraus 2009, Meshaka 2008, Phillips et al. 2003), especially in Florida where 3
recent papers have described the current invasion by reptiles and amphibians as
“aggressive” and “a runaway train” (Engeman et al. 2011, Krysko et al. 2011a, Meshaka
2011). South Florida has proven to be particularly vulnerable to invasion by
reptiles because it has a subtropical climate, a disturbed natural environment that
provides suitable habitats for invasive species (ponds, canals, and levees), and major
sources of non-native species from the pet trade (port of entry, captive breeders,
and animal dealers) (Butterfield et al. 1997, Wilson and Porras 1983). As a result,
Florida currently has more species of introduced and established reptiles than any
other state, and the rate of accumulation of new species is increasing rapidly (Krysko
et al. 2011a, b; Meshaka 2011).
There are more species of non-native lizards reproducing in Florida than
native species. The 4 largest lizards breeding in Florida are from Africa, South
America, and Central America (Engeman et al. 2011). A population of Tupinambis
merianae Duméril and Bibron (Argentine Black and White Tegu) exists
in parts of Hillsborough and Polk counties in west-central Florida (Enge 2007,
Krysko et al. 2011b). Argentine Black and White Tegus are omnivorous and primarily
terrestrial, although they are good swimmers (Achaval 1977, Cei 1986).
1National Park Service, Biological Resources Management Division, Florida/Caribbean
Exotic Plant Management Team, 18001 Old Cutler Road, Suite 419, Palmetto Bay, FL
33157-6422. 2Florida Fish and Wildlife Conservation Commission, Rookery Bay NERR,
300 Tower Road, Naples, FL 34113. 3University of Florida, 3205 College Avenue, Davie,
FL 33314. *Corresponding author - firstname.lastname@example.org.
766 Southeastern Naturalist Vol. 11, No. 4
The Argentine Black and White Tegu is an active burrower and spends a lot of
time in burrows to avoid extremes in temperature (Abe 1995, Andrade and Abe
In addition to their breeding population, Argentine Black and White Tegus
have been sighted in various locations elsewhere in Florida, especially in Miami-
Dade County in southeastern Florida (Engeman et al. 2011, Krysko et al. 2011b).
However, no evidence has been published for reproduction. Here, we report the
first observations of nesting of the Argentine Black and White Tegu in southeastern
Methods and Results
In response to numerous observations of Argentine Black and White Tegus in
southern Miami-Dade County, partners of the Everglades Cooperative Invasive
Species Management Area (ECISMA) began an assessment of the status of a potential
population. This assessment included reconnaissance surveys by vehicle
and foot, camera trapping, live trapping, and radio telemetry of tegus.
In 2010, 17 live traps were deployed at various locations in Florida City,
Miami-Dade County, including one at the Miami-Dade Juvenile Residential
Facility (25°22.3'N, 80°28.9'W), using fresh chicken eggs as bait. Trapping was
initiated on 27 April and concluded on 27 September. Traps were opened and
checked daily from Monday through Friday and were closed on the weekends,
for a total of 1849 trap nights (109 trap nights at the Miami-Dade Juvenile Residential
We trapped a total of 124 Argentine Tegus. On 9 September 2010, we collected
a female Argentine Tegu at the Miami-Dade Juvenile Residential Facility
in a live trap. We surgically implanted a VHF radio transmitter on 30 September
2010, and the female was released at the residential facility on 4 October 2010. A
total of 36 radio-telemetry locations were recorded between 4 October 2010 and
7 June 2011 when the female was recaptured in a live trap. Sixteen locations were
within a ruderal thicket dominated by invasive exotic plants on the western side
of the residential facility, and upon investigation, a nest mound was discovered
in the thicket (25°22.389'N, 80°28.924'W).
The habitat surrounding the Miami-Dade Juvenile Detention Center is disturbed
short-hydroperiod marl prairie consisting of a mixture of wet prairie,
Cladium jamaicense Crantz (Sawgrass), tree islands, and tropical hammock plant
communities. The detention center facility and fenced grounds is constructed on
approximately 20 acres of limestone fill. The majority of the detention center’s
land is maintained by regular mowing. The northern perimeter of the detention
center is unmaintained and, as a result of substrate disturbance, was heavily
colonized by invasive exotic species such as Schinus terabinthafolius Raddi
(Brazilian Pepper), Leucaena leucocephala (Lam.) deWit (Lead Tree), Albizia
lebbeck (L.) Benth (Woman’s Tongue), Ricinus communis L. (Castor Bean), and
Nephrolepis cordifolia (L.) K. Presl (Sword Fern). Native species present were
typical of disturbed sites and included Salix spp. (willow), Baccharis halimifolia
L. (Eastern Baccharia), Bidens alba L. (Shephard’s Needles), and Lippia nodiflora
L. (Frog Fruit).
The nest mound was composed of discarded potting soil, decomposed organic
material, and detritus at the base of a Lead Tree stump covered by Syngonium
podophyllum Schott (Arrowhead Vine), a non-native invasive species (Fig. 1).
The nest mound was located approximately 7 m west of the eastern edge of the
2012 T. Pernas, D.J. Giardina, A. McKinley, A. Parns, and F.J. Mazzotti 767
Figure 1. Nest mound (top) and excavated nest (bottom) of the telemetered Argentine
Black and White Tegu at the Miami-Dade Juvenile Residential Facility. Nest was located
at the base of a Lead Tree stump.
768 Southeastern Naturalist Vol. 11, No. 4
thicket. On 9 June 2011, we excavated the suspected nest mound (203 cm x 152
cm x 61 cm) by removing vines and systematically dismantling it using hand
tools (Fig. 1). We uncovered a nest chamber (33 cm x 23 cm x 15 cm) in the approximate
center of the mound, containing a clutch of 21 eggs at a depth (to top
of clutch) of 41 cm. During excavation, 2 eggs were damaged and 1 was opened
to verify the species and to estimate age of development. The remaining 18 eggs
were collected. A second, older nest chamber (37 cm x 20 cm x 20 cm) was
unearthed just behind and below the first one at a depth of 44 cm. The older nest
was comprised of 22 hatched egg shells and 13 unhatched eggs. A colony of the
non-native Solenopsis invicta Buren (Red Imported Fire Ant) was disturbed by
excavation of the nest mound. There was no evidence that the ants’ presence had
negatively impacted tegu nesting.
There is growing evidence that the number of established non-native reptiles
and amphibians, as well as their respective populations and ranges, are increasing
rapidly in Florida (Krysko et al. 2011a, b; Meshaka 2011). Our data provide
the first evidence confirming expansion of a reproducing population of Argentine
Black and White Tegus into southeastern Florida. If this population is small and
localized, there is potential for eradication if swift, decisive action is taken.
As with Python molurus bivittatus Kuhl (Burmese Python) (Snow et al. 2007),
radio telemetry proved to be an effective technique for documenting presence
of Argentine Black and White Tegu nests. The clutch sizes found (21 this year
and 35 from earlier) are within the range of 20 to 50 eggs reported for Argentine
Tegus (Donadío and Gallardo 1984) in their native range. Pierre (pers. comm. in
Enge 2007) predicted that tegu nests would be constructed at the base of a tree or
under a log or other surface object as we found in southeastern Florida.
In its native range, the Argentine Black and White Tegu occurs in forested,
open, and disturbed habitats (Fitzgerald 1994). Tegus can be found in wet areas
such as flooded savannas and streams (Norman 1987), and they also seem to prefer
areas with opportunities for burrows (Balsai 1998). In west-central Florida, Argentine
Black and White Tegus have been found in natural (scrub) habitats, especially
in association with Gopher Tortoise, Gopherus polyphemus (Daudin) burrows
(Enge 2007, Engeman et al. 2011). Our study area is comprised of disturbed habitat
and is in close proximity to water with artificially elevated areas for nests and burrows.
This habitat feature is commonly found along canals and ponds surrounding
our study area and throughout southern Florida. From telemetry data, we have
evidence of tegus dispersing from our study area along and across canals (unpubl.
data). Without control, it is possible that this population will expand to other areas,
especially along and across canals, levees, and roads.
Tegus are known to be egg predators (Achaval 1977, Escalona and Fa 1998).
In southeastern Florida, their presence could endanger nests of sea turtles, Alligator
mississippiensis (Daudin) (American Alligator), and Crocodylus acutus
(Cuvier) (American Crocodile). Nests of American Crocodiles at the Florida
Power and Light Company’s Turkey Point Power Plant site are particularly at risk
since they are within dispersal distance (10 km) of current locations of tegus.
Although adverse impacts of the Argentine Black and White Tegu have yet
to be detected, management action is warranted before individuals disperse farther
in the region. Waiting to act would limit management options, decrease the
probability that they will be successful, and ensure that they are more expensive
2012 T. Pernas, D.J. Giardina, A. McKinley, A. Parns, and F.J. Mazzotti 769
(Byers et al. 2002). Since we know that Argentine Tegus are established (reproducing)
in Florida, the time for action is when individual tegus and nests are first
discovered at new locations prior to detection of detrimental impacts.
This study was supported by the National Park Service and the Florida Fish and
Wildlife Conservation Commission. Preparation of the manuscript was supported by the
University of Florida. We thank Rebecca Harvey and Sara Williams for formatting and
editing this manuscript. Walter Meshaka, Kenneth Krysko, Jennifer Eckles, and Scott
Hardin provided valuable comments that greatly improved this manuscript. All permits
and approvals for this study were obtained from the Florida Fish and Wildlife Conservation
Committee (EXOT-12-107) and the Animal Research Committee at the University
of Florida (001-10FTL).
Abe, A.S. 1995. Estivation in South American amphibians and reptiles. Brazilian Journal
of Medical and Biological Research 28:1241–1247.
Achaval, F. 1977. Lista comentada de los reptiles que habitan en la zona de influencia
de la represa de Salto Grande. Seminario Medio Ambiente y Represas, Montevideo
Andrade, D.V., and A.S. Abe. 1999. Gas exchange and ventilation during dormancy in the
tegu lizard Tupinambis merianae. Journal of Experimental Biology 202:3677–3685.
Balsai, M. 1998. Tegus: South America’s cunning teiids. Reptiles 6(9):52–69.
Bomford, M., F. Kraus, S.C. Barry, and E. Lawrence. 2009. Predicting establishment
success for alien reptiles and amphibians: A role for climate matching. Biological
Butterfield, B.P., W.E. Meshaka, Jr., and C. Guyer. 1997. Nonindigenous amphibians
and reptiles. Pp. 123–138, In D. Simberloff, D.C. Schmitz, and T.C. Brown (Eds.).
Strangers in Paradise: Impact and Management of Nonindigenous Species in Florida.
Island Press, Covelo, CA. 467 pp.
Byers, J.E., S. Reichard, J.M. Randall, I.M. Parker, C.S. Smith, W.M. Lonsdale, I.A.E.
Atkinson, T.R. Seastedt, M. Williamson, E. Chornesky, and D. Hayes. 2002. Directing
research to reduce the impacts of nonindigenous species. Conservation Biology
Cei, J.M. 1986. Reptiles del Centro, Centro-Oeste y Sur de la Argentina. Herpetofauna de
las Zonas Áridas y Semiáridas. Monografia 4, Museo Regionale di Scienze Naturali,
Torino, Italy. 527 pp.
Donadío, O.E., and J.M. Gallardo. 1984. Biología y conservación de las especies del
género Tupinambis (Squamata, Sauria, Teiidae) en la República Argentina. Revista
del Museo Argentina de Ciencias Naturales “Bernardino Rivadavia” (Zoologia)
Enge, K.M. 2007. FWC Bioprofile for the Argentine Black and White Tegu (Tupinambis
merianae). Florida Fish and Wildlife Conservation Commission Report, Tallahassee,
FL. 27 pp.
Engeman, R., E. Jacobson, M.L. Avery, and W.E. Meshaka, Jr. 2011. The aggressive invasion
of exotic reptiles in Florida with a focus on prominent species: A review. Current
770 Southeastern Naturalist Vol. 11, No. 4
Escalona, T., and J.E. Fa. 1998. Survival of nests of the Terecay Turtle (Podocnemis
unifilis) in the Nichara-Tawadu rivers, Venezuela. Journal of Zoology 244:303–312.
Fitzgerald, L.A. 1994. The interplay between life history and environmental stochasticity:
Implications for the management of exploited lizard populations. American
Kraus, F.R. 2009. Alien Reptiles and Amphibians: A Scientific Compendium and Analysis.
Springer, New York, NY. 563 pp.
Krysko, K.L., J.P. Burgess, M.R. Rochford, C.R. Gillette, D. Cueva, K.M. Enge, L.A.
Somma, J.L. Stabile, D.C. Smith, J.A. Wasilewski, G.N. Kieckhefer III, M.C.
Granatosky, and S.V. Nielsen. 2011a. Verified non-indigenous amphibians and reptiles
in Florida from 1863 through 2010: Outlining the invasion process and identifying
invasion pathways and stages. Zootaxa 3028:1–64.
Krysko, K.L., K.M. Enge, and P.E. Moler. 2011b. Atlas of amphibians and reptiles in
Florida. Final Report, Project Agreement 08013, Florida Fish and Wildlife Conservation
Commission, Tallahassee, FL. 524 pp.
Meshaka, W.E., Jr. 2008. The exotic amphibians and reptiles of the United States. Pp.
24–35, In G.J. Graeter, K.A. Buhlmann, L.R. Wilkinson, and J.W. Gibbons (Eds.).
Inventory and Monitoring: Recommended Techniques for Reptiles and Amphibians,
with Application to the United States and Canada. PARC Technical Report,
Meshaka, W.E., Jr. 2011. A runaway train in the making: The exotic amphibians, reptiles,
turtles, and crocodilians of Florida. Monograph 1. Herpetological Conservation and
Norman, D.R. 1987. Man and tegu lizards in eastern Paraguay. Biological Conservation
Parker, I.M., D. Simberloff, W.M. Lonsdale, K. Goodell, M. Wonham, P.M. Kareiva,
M.H. Williamson, B.V. Holle, P.B. Moyle, J.E. Byers, and L. Goldwasser. 1999.
Impact: Toward a framework for understanding the ecological effects of invaders.
Biological Invasions 1:3–19.
Phillips, B.L., G.P. Brown, and R. Shine. 2003. Assessing the potential impact of Cane
Toads on Australian snakes. Conservation Biology 17:1738–1747.
Snow, R.W., V.M. Johnson, M.L. Brien, M.S. Cherkiss, and F.J. Mazzotti. 2007. Python
molurus bivittatus: Nesting. Herpetological Review 38:93.
Wilcove D.S., D. Rothstein, J. Dubow, A. Phillips, and E. Losos. 1998. Quantifying
threats to imperiled species in the United States. Bioscience 48:607–615.
Wilson, L.D., and L. Porras. 1983. The ecological impact of man on the south Florida
herpetofauna. Special Publication No. 9, University of Kansas Museum of Natural
History and World Wildlife Fund-US, Lawrence, KS. 89 pp.