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  • Cuban Tree Frog  (Photo: Ltshears,  www.commons.wikimedia.org)
  • Osteopilus septentrionalis (Photo: Ansel Fong, http://calphotos.berkeley.edu via www.commons.wikimedia.org)
  • Hyla septentrionalis (Photo: Holger Gr�schl, www.naturspektrum.de via www.commons.wikimedia.org)
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Common name
rana cubana (English), rana platernera (Spanish), Giant Tree-frog (English), Marbled Tree-toad (English), Cuban Treefrog (English)
Synonym
Trachycephalus insulsus , Cope, 1864
Trachycephalus wrightii , Cope, 1864
Hyla schebestana , Werner, 1917
Hyla microterodisca , Werner, 1921
Trachycephalus marmoratus , Dum�ril & Bibron, 1841
Osteopilus septentrionalis , Dum�ril & Bibron, 1841
Hyla lesueurii , Bory de Saint-Vincent, 1828
Hyla sueurri , Bory de Saint-Vincent, 1831
Dendrohyas septentrionalis , Tschudi, 1838
Trachycephalus septentrionanlis , Barbour, 1904
Hyla dominicensis septentrionalis , Mertens, 1939
Hyla insulsa , Mittleman, 1950
Hyla dominicensis insulsa , Mittleman, 1950
Similar species
Summary
The Cuban treefrog, Osteopilus septentrionalis is a voracious, nocturnal predator that eats any prey that it can grab, including members of its own species, other frogs, lizards, insects, spiders, and small snakes. It is an arboreal species, but it can also survive in moist areas. It is an excellent climber and is variable in color. This species is a threat to native species primarily through predation and competition. The Cuban treefrog is easily distinguishable from other frogs by its comparably large size and warty skin. This species is very successful in colonizing and has a long life span, which can make it a very significant problem in regions where it is introduced.
Notes
Recent increases in shipping and trade, as well as increasing human populations and demands for non-regional produce and landscaping and building materials have enabled the dispersal and invasion of the Cuban treefrog (Platenberg, 2007). The Cuban treefrog is a storm-adapted species that can immediately increase its fecundity and rapidly disperse during and after hurricanes (Somma, 2008). High fecundity, a short larval period, broad diet, open habitat, and dietary niches make this species a successful widespread anuran population in situations that seem less than ideal for supporting it (Townsend, Eaton, Powell et al, 2000).
Lifecycle Stages
Eggs are around 3 mm when they hatch into tadpoles. Tadpoles typically emerge between 1 and 2 days after the eggs are laid (GSMFC, 2007). At about 20 hours after hatching, tadpoles are around 2 mm from snout to vent with a tail length of about 4 mm. They reach a size of 26-32 mm at metamorphosis, which occurs usually 30-60 days after hatching. The Cuban treefrog is a long-lived species with a lifespan of approximately 5-10 years (Masterson, 2007). Males tend to exhibit lower survival than females, which means that females have more time to grow than males. Males in some populations tend to live in a mature stage up to 3 months, whereas mature females can live more than 2 years. Due to the fact that there is a positive relationship between the snout, vent length and the number of eggs that are laid, research indicates that females mature more slowly than males, and they skip breeding events. However, there is no difference in the growth rates of male and female juveniles (Salinas, 2006a).
Uses
The Cuban treefrog has been used in the form of a pet as well as a display animal and in international horticulture. In fact, it has been reported that a large percentage of this species has been a part of captive breeding/farming at some point (Hedges et al, 2008).
Habitat Description
Osteopilus septentrionalis occurs from sea level up to 1,110m asl. Cuban treefrogs live in mesic habitats but may also be found in xeric habitats. This species can tolerate brackish water, which includes pools, marshes, flood pastures, and ditches (Hedges et al, 2008). Terrestrial habitats include forest-hardwood, mixed, suburban/orchard as well as woodland of conifers or mixed. Daytime retreats include surface objects, hollow logs, burrows, high corners of beams of rooms, and nests of birds to name a few. Larvae are aquatic (NatureServe, 2008). In addition, O. septentrionalis can easily coexist among humans. In fact, this species can be many times more numerous in urban habitats than any of its natural habitats (Meshaka, 1996a). The Cuban treefrog has been encountered in mangrove scrub and mangrove in addition to disturbed areas (Rice, Waddle, Crockett et al, 2007). O. septentrionalis is well known for exploiting man-made structures and water supplies, which results in the successful colonization of certain areas (Townsend, Eaton, Powell et al, 2000). This species has also occurred in agricultural settings such as orange groves and plant nurseries. It may also be found in small trees and shrubs, being an arboreal animal, and has even been found buried several inches below dry soil (Johnson, 2007).
Reproduction
Osteopilus septentrionalis reproduces at night and is largely stimulated by rainfall, especially warm summer rains (Johnson, 2007). Males have horny nuptial excrescenses on their thumbs and a medial internal subgular vocal sac with posterolateral extensions (GSMFC, 2007). The vocal sac, which is located under the chin and when inflated has the appearance of a double sac, is used to make breeding calls. The fairly distinct calls of the male Cuban treefrog sounds like a squeaking door or a \"snoring rasp\" (Johnson, 2007). Males call from leaves, branches, limbs and stems of saplings (NatureServe, 2008). Breeding is non-assortive by the snout, vent length. However, males may increase their reproductive success by starting to breed with small snout, vent length females and by participating in all possible breeding events, and they apparently start to breed at a younger age than females (Salinas, 2006a). Males do not exhibit any parental care nor do they defend territories. Unpaired males often clasp males in amplexus or place themselves alongside other mated pairs (Salinas, 2006b). Females lay approximately 130 eggs, which are deposited in lakes, pools, cisterns, etc (GSMFC, 2007). However, the number of eggs deposited by the female is related to her size. A very large female may lay an excess of 15,000 eggs in one season (Johnson, 2007). The Cuban treefrog is capable of using pools of relatively high salinity for reproduction. Eggs form a thin floating sheet at the surface (GSMFC, 2007 ). Breeding events typically last only one night (Salinas, 2006b).
Nutrition
The Cuban treefrog is a \"sit and wait\" predator that feeds at night (Johnson, 2007). This species is a voracious predator that preys on any small animal that it can catch, especially insects, spiders, and other small frogs (GSMFC, 2007). This species is also known to eat lizards and small snakes (Johnson, 2007). Research concluded that there is no apparent trend in the size or hardness when looking at the composition of the diet or individual prey items present in the diet of the Cuban treefrog (Owen, 2005).
Pathway
Recent increases in shipping, along with increasing human populations and demands for non-regional produce and landscaping building materials have enabled the dispersal of opportunisitc invaders such as the Cuban treefrog (Platenberg, 2007).This species has been used as pets and display animals (Hedges et al, 2008).

Principal source:

Compiler: National Biological Information Infrastructure (NBII), Comité français de l'UICN (IUCN French Committee) & IUCN SSC Invasive Species Specialist Group (ISSG)

Review:

Publication date: 2008-03-14

Recommended citation: Global Invasive Species Database (2024) Species profile: Osteopilus septentrionalis. Downloaded from http://iucngisd.org/gisd/speciesname/Osteopilus+septentrionalis on 21-12-2024.

General Impacts
The Cuban treefrog has sticky skin secretions that can be extremely irritating to the mucous membranes of people. The secretions can cause a burning and itching sensation that can sometimes last for more than an hour. It can also be a nuisance to people because of its many abundant hiding places, consistent food sources, and adequate breeding sites that are many times provided by human dominated landscapes where populations may become quite dense. The standard of living may be lowered in areas where the Cuban treefrog prospers. For example, this species has been found in toilet bowls and has clogged drains. The mating calls of male Cuban treefrogs can be an annoyance as well (Johnson, 2007). The Cuban treefrog may also be a vector of pathogens (Hedges et al, 2008). Studies suggest that this species has the potential to inflict substantial monetary and ecological damage on the habitat that it invades (Owen, 2005). Adults are predators to native animals in areas of invasion, but larvae can also be threatening. Cuban treefrogs as tadpoles will prey on heterospecific anuran larvae, which may reduce the survivorship of these heterospecific tadpoles (Smith, 2005a).
Management Info
Preventative measures: Early detection and rapid response are very important for a rapid and successful eradication of this species in introduced areas (Campbell, 2008).

Biological: Some species of aquatic and terrestrial species of snake are predators of the Cuban treefrog (GSMFC, 2007).

Integrated management: Effectively screening cisterns and regulating water distribution will negatively impact established populations of Cuban treefrog (Townsend, Eaton, Powell, et al, 2000).

Chemical: Monitoring and fumigating imported plants should impair further dispersal of the species (Townsend, Eaton, Powell et al 2000).

Countries (or multi-country features) with distribution records for Osteopilus septentrionalis
Informations on Osteopilus septentrionalis has been recorded for the following locations. Click on the name for additional informations.
Lorem Ipsum
Location Status Invasiveness Occurrence Source
Details of Osteopilus septentrionalis in information
Status
Invasiveness
Arrival date
Occurrence
Source
Introduction
Species notes for this location
Location note
Management notes for this location
Impact
Mechanism:
Outcome:
Ecosystem services:
Impact information
The Cuban treefrog has sticky skin secretions that can be extremely irritating to the mucous membranes of people. The secretions can cause a burning and itching sensation that can sometimes last for more than an hour. It can also be a nuisance to people because of its many abundant hiding places, consistent food sources, and adequate breeding sites that are many times provided by human dominated landscapes where populations may become quite dense. The standard of living may be lowered in areas where the Cuban treefrog prospers. For example, this species has been found in toilet bowls and has clogged drains. The mating calls of male Cuban treefrogs can be an annoyance as well (Johnson, 2007). The Cuban treefrog may also be a vector of pathogens (Hedges et al, 2008). Studies suggest that this species has the potential to inflict substantial monetary and ecological damage on the habitat that it invades (Owen, 2005). Adults are predators to native animals in areas of invasion, but larvae can also be threatening. Cuban treefrogs as tadpoles will prey on heterospecific anuran larvae, which may reduce the survivorship of these heterospecific tadpoles (Smith, 2005a).
Locations
ANGUILLA
JAMAICA
SAINT BARTHELEMY
SAINT MARTIN (FRENCH PART)
UNITED STATES
VIRGIN ISLANDS, U.S.
Mechanism
[5] Competition
[4] Predation
Outcomes
[7] Environmental Ecosystem - Habitat
  • [2] Modification of hydrology/water regulation, purification and quality /soil moisture
  • [5] Reduction in native biodiversity
[2] Socio-Economic
  • [2] Damage to infrastructures
Management information
Preventative measures: Early detection and rapid response are very important for a rapid and successful eradication of this species in introduced areas (Campbell, 2008).

Biological: Some species of aquatic and terrestrial species of snake are predators of the Cuban treefrog (GSMFC, 2007).

Integrated management: Effectively screening cisterns and regulating water distribution will negatively impact established populations of Cuban treefrog (Townsend, Eaton, Powell, et al, 2000).

Chemical: Monitoring and fumigating imported plants should impair further dispersal of the species (Townsend, Eaton, Powell et al 2000).

Bibliography
84 references found for Osteopilus septentrionalis

Management information
Anguilla National Trust., 29th May 2007. Anguilla Invasive Species. Workshop Report 29th May 2007 Paradise Cove Hotel, Anguilla
Summary: Available from: http://www.scscb.org/working_groups/resources/invasives-workshop-report-anguilla.pdf [Accessed 4 September 2008]
Centre for Environment, Fisheries & Aquaculture Science (CEFAS)., 2008. Decision support tools-Identifying potentially invasive non-native marine and freshwater species: fish, invertebrates, amphibians.
Summary: The electronic tool kits made available on the Cefas page for free download are Crown Copyright (2007-2008). As such, these are freeware and may be freely distributed provided this notice is retained. No warranty, expressed or implied, is made and users should satisfy themselves as to the applicability of the results in any given circumstance. Toolkits available include 1) FISK- Freshwater Fish Invasiveness Scoring Kit (English and Spanish language version); 2) MFISK- Marine Fish Invasiveness Scoring Kit; 3) MI-ISK- Marine invertebrate Invasiveness Scoring Kit; 4) FI-ISK- Freshwater Invertebrate Invasiveness Scoring Kit and AmphISK- Amphibian Invasiveness Scoring Kit. These tool kits were developed by Cefas, with new VisualBasic and computational programming by Lorenzo Vilizzi, David Cooper, Andy South and Gordon H. Copp, based on VisualBasic code in the original Weed Risk Assessment (WRA) tool kit of P.C. Pheloung, P.A. Williams & S.R. Halloy (1999).
The decision support tools are available from: http://cefas.defra.gov.uk/our-science/ecosystems-and-biodiversity/non-native-species/decision-support-tools.aspx [Accessed 13 October 2011]
The guidance document is available from http://www.cefas.co.uk/media/118009/fisk_guide_v2.pdf [Accessed 13 January 2009].
Christy, Michelle T; Savidge, Julie A; Rodda, Gordon H., 2007. Multiple pathways for invasion of anurans on a Pacific island. Diversity & Distributions. 13(5). SEP 2007. 598-607.
Gregoire, D. R., 2005. Tadpoles of the Southeastern United States Coastal Plain. United States Geological Survey Report. Florida Integrated Science Center. 60pp
Summary: Identification aid.
Available from: http://www.cnah.org/pdf_files/430.pdf [Accessed 4 September 2008]
Platenberg, Renata J.; Boulon, Ralf H., 2006. Conservation status of reptiles and amphibians in the U.S. Virgin Islands. Applied Herpetology, Volume 3, Number 3, 2006 , pp. 215-235(21)
Varnham, K. 2006. Non-native species in UK Overseas Territories: a review. JNCC Report 372. Peterborough: United Kingdom.
Summary: This database compiles information on alien species from British Overseas Territories.
Available from: http://www.jncc.gov.uk/page-3660 [Accessed 10 November 2009]
Goetz SM, Guyer C, Boback SM, Romagosa CM (2018) Toxic, invasive treefrog creates evolutionary trap for native gartersnakes. Biological invasions 20 (2): 519-531.
Haggerty CJ, Crisman TL (2015) Pulse disturbance impacts from a rare freeze event in Tampa, Florida on the exotic invasive Cuban treefrog, Osteopilus septentrionalis, and native treefrogs. Biological Invasions 17 (7): 2103-2111.
Ortega N, Price W, Campbell T, Rohr J (2015) Acquired and introduced macroparasites of the invasive Cuban treefrog, Osteopilus septentrionalis. International Journal for Parasitology: Parasites and Wildlife 4 (3): 379-384.
Tennessen JB, Parks SE, Tennessen TP, Langkilde T (2016) Raising a racket: invasive species compete acoustically with native treefrogs. Animal Behaviour 114: 53-61.
Tennessen J, Parks SE, Snow RW, Langkilde TL (2013) Impacts of acoustic competition between invasive Cuban treefrogs and native treefrogs in southern Florida. InProceedings of Meetings on Acoustics ICA 19 (1): 010057. Acoustical Society of America.
General information
Andrews JM, Childress JN, Iakovidis TJ, Langford GJ (2015) Elucidating the life history and ecological aspects of Allodero hylae (Annelida: Clitellata: Naididae), a parasitic oligochaete of invasive Cuban tree frogs in Florida. Journal of Parasitology 101 (3): 275-281.
Bartareau, Tad M., 2004. PVC pipe diameter influences the species and sizes of treefrogs captured in a Florida coastal oak scrub community. Herpetological Review. 35(2). June 2004. 150-152.
Bartareau, Tad M; Meshaka, Walter E., 2007. Osteopilus septentrionalis (Cuban treefrog). Diet. Herpetological Review. 38(3). SEP 2007. 324-325.
Breuil, M. 2002. Histoire naturelle des Amphibiens et des Reptiles terrestres de l archipel Guadeloup�en. In Patrimoines Naturels, MNHN, Paris.
Summary: Ce livre propose une synth�se sur les amphibiens et reptiles terrestres de l archipel Guadeloup�en. Six esp�ces d anoures, 5 de tortues, 21 de l�zards dont 4 �teintes et 7 de serpents sont d�taill�es.
Breuil, M. & Ib�n�, B. 2004. Les Hylides invasifs dans les Antilles fran�aises et le peuplement batrachologique naturel. Bull. Soc. Herpetol. Fr, 10 p.
Summary: Synth�se des introductions d hylides (rainettes) dans les Antilles fran�aises. Trois esp�ces exotiques et envahissantes sont inventori�es.
Breuil, Michel - Ed. 2003. Osteopilus septentrionalis. Museum national d histoire naturelle de Paris (Paris- 2002)
Summary: Rapport scientifique sur la rainette de Cuba. Sont pr�sent�s sa syst�matique, sa r�partition dans l archipel Guadeloup�en, son habitat, sa biologie, etc
Available from: http://sxm.fauna.free.fr/Rep/A-Osteopilus-septentrionalis.htm [Accessed 7 April 2008]
Campbell, Todd S., 2007. Osteopilus septentrionalis (Cuban Treefrog). Saurophagy. Herpetological Review. 38(4). DEC 2007. 440.
Cayman Wildlife Connection., 2004. Amphibians and Reptiles in the Cayman Islands
Summary: Available from: http://www.caymanwildlife.org/docs/Amphib-Reptiles.doc [Accessed 4 September 2008]
Christman, Steven P; Young, Cameron A; Gonzalez, Shannon; Hill, Karen; Navratil, George; Delis, Pablo., 2000. New records of amphibians and reptiles from Hardee County, Florida. Herpetological Review. 31(2). June, 2000. 116.
Daltry, Jennifer, C., 2007. An introduction to the herpetofauna of Antigua, Barbuda and Redonda, with some conservation recommendations. Applied Herpetology, Volume 4, Number 2, 2007 , pp. 97-130(34)
Dodd, C. Kenneth, Jr; Griffey, Marian L., 2002. Remarks on the current status of the non-marine herpetofauna of Egmont Key, Florida. Florida Scientist. 65(1). Winter, 2002. 62-66
Summary: Abstract: The present, non-marine herpetofauna of Egmont Key consists of three (possibly four) snakes, two (possibly five) lizards, two turtles, and three frogs. Three species (Cuban Treefrog, Osteopilus septentrionalis; Indo-Pacific Gecko, Hemidactylus garnotii; Cornsnake, Elaphe guttata) are reported for the first time. The Cuban Treefrog and Indo-Pacific Gecko likely arrived with construction material; the sole Cornsnake may have been a released captive. There are no recent records of three species (Green Treefrog, Hyla cinerea; Mole Skink, Eumeces egregius; Eastern Diamond-backed Rattlesnake, Crotalus adamanteus). The Green Anole (Anolis carolinensis), thought extirpated, was resighted in 1998. This species may have recently recolonized or been transported to the island rather than have persisted unseen for more than 90 years.
Forys, Elizabeth A. & Craig R. Allen., 1998. Biological invasions and deletions: community change in south Florida. Biological Conservation Volume 87, Issue 3, (March 1999) Pages 341-347
Franz, Richard, C; Kenneth Dodd Jr.; & Donald W. Buden., 1993. Distributional Records of Amphibians and Reptiles from the Exuma Islands, Bahamas, Including the First Reports of a Freshwater Turtle and an Introduced Gecko. Caribbean Journal of Science, Vol. 29, No. 3-4, 165-173, 1993
Global Biodiversity Information Facility (GBIF), 2008. Species: Osteopilus septentrionalis Dum�ril & Bibron, 1841.
Summary: Available from: http://data.gbif.org/species/13847304 [Accessed 15 June 2010]
Gulf States Marine Fisheries Commission (GSMFC)., 2007. Osteopilus septentrionalis (Dum�ril and Bibron, 1841)
Summary: Available from: http://nis.gsmfc.org/nis_factsheet.php?toc_id=206 [Accessed 4 September 2008]
Guzy, Jackie C; Campbell, Todd S; Campbell, Kym Rouse., 2006. Effects of hydrological alterations on frog and toad populations at Morris Bridge Wellfield, Hillsborough County, Florida. Florida Scientist. 69(4). FAL 2006. 276-287.
Summary: Amphibian populations worldwide have been declining for decades, largely due to habitat destruction, water pollution, and introduced species. Wetland impacts are often the cause of local amphibian declines. We studied the effect of alterations in wetland hydrology on frog and toad populations at Morris Bridge Wellfield (MBWF) in Hillsborough County, Florida. Frogs and toads in wetlands in zones of different surficial aquifer drawdown levels were studied to determine if hydrological differences resulting from groundwater pumping affected their populations. Nighttime call surveys and tadpole sampling were conducted at 16 wetlands in three drawdown zones from June through August 2004. While there was no significant relationship between the number of tadpole species and drawdown zone, the zone unaffected by groundwater pumping had significantly higher tadpole densities than the other zones. No correlation was found between the number of species calling in each wetland and the number of tadpole species captured. Cuban treefrogs (Osteopilus septentrionalis), an introduced species that competes with and consumes native frogs, comprised 48% of tadpoles captured and were found at 50% of the wetlands studied. This marks the beginning of a long-term study of the interaction between the impacts of hydrological alterations and introduced species on native frogs and toads at MBWF.
ITIS (Integrated Taxonomic Information System), 2008. Online Database Osteopilus septentrionalis (Dum�ril and Bibron, 1841)
Summary: An online database that provides taxonomic information, common names, synonyms and geographical jurisdiction of a species. In addition links are provided to retrieve biological records and collection information from the Global Biodiversity Information Facility (GBIF) Data Portal and bioscience articles from BioOne journals.
Available from: http://www.itis.gov/servlet/SingleRpt/SingleRpt?search_topic=TSN&search_value=173538 [Accessed 11 March 2008]
Johnson, Steve A., 2007. Osteopilus septentrionalis (Cuban treefrog). Herpetological Review. 38(3). SEP 2007. 349.
Johnson, Steve A; Staiger, Jennifer S; Barichivich, William J; Barlow, Steve., 2003. Osteopilus septentrionalis (Cuban treefrog). Herpetological Review. 34(4). December 2003. 381.
Krysko, Kenneth L; Enge, Kevin M; Townsend, Josiah H; Langan, Esther M; Johnson, Steve A; Campbell, Todd S., 2005. New county records of amphibians and reptiles from Florida. Herpetological Review. 36(1). MAR 05. 85-87.
Krysko, Kenneth L; King, F. Wayne., 1999. Osteopilus septentrionalis (Cuban treefrog). Herpetological Review. 30(4). Dec., 1999. 230-231.
Lindsay, Kevel & Cooper, Brian., 2008. Osteopilus septentrionalis becomes established on Antigua, West Indies. Applied Herpetology, Volume 5, Number 1, 2008 , pp. 96-98(3)
Livo, Lauren J., Geoffrey A. Hammerson, Hobart M. Smith., 1998. Summary of Amphibians and Reptiles Introduced into Colorado. Northwestern Naturalist, Vol. 79, No. 1 (Spring, 1998), pp. 1-11
Lorvelec, O., Pascal., M., Pavis, C., Feldmann, P. 2007. Amphibians and reptiles of the French West Indies : Inventory, threats and conservation. Applied Herpetology 4, 131-161
Summary: Cet article fait le point des connaissances sur les amphibiens et les reptiles indig�nes et introduits des Antilles fran�aises. Les impacts des esp�ces introduites sur la faune indig�ne sont discut�s. Le cas de la conservation des populations d Iguana delicatissima sur l�le de Petite-Terre est pr�sent�
Love, William B., 1995. Anura: Osteopilus septentrionalis (Cuban treefrog). Predation. Herpetological Review. 26(4). 1995. 201-202.
Malhotra, Anita; Thorpe, Roger S; Hypolite, Eric; James, Arlington., 2007. A report on the status of the herpetofauna of the Commonwealth of Dominica, West Indies. Applied Herpetology, Volume 4, Number 2, 2007 , pp. 177-194(18)
Masterson, J., 2007. Species Name: Osteopilus septentrionalis Common Name: (Cuban Treefrog). Smithsonian Marine Station at Fort Pierce
Summary: Available from: http://www.sms.si.edu/irlspec/Osteopilus_septentrionalis.htm [Accessed 4 September 2008]
Meshaka, Walter E. Jr., 1996a. Diet and the colonization of buildings by the Cuban treefrog, Osteopilus septentrionalis (Anura: Hylidae). Caribbean Journal of Science. 32(1). 1996. 59-63.
Meshaka, Walter E. Jr., 1996. Anura: Osteopilus septentrionalis (Cuban treefrog). Maximum size. Herpetological Review. 27(2). 1996. 74.
Meshaka, Walter E. Jr., 1996b. Retreat use by the Cuban treefrog (Osteopilus septentrionalis): Implications for successful colonization in Florida. Journal of Herpetology. 30(3). 1996. 443-445.
Meshaka, Walter E. Jr., 1996. Vagility and the Florida distribution of the Cuban treefrog (Osteopilus septentrionalis). Herpetological Review. 27(1). 1996. 37-40.
Meshaka, Walter E., Jr., 1999. The herpetofauna of the Doc Thomas House in South Miami, Florida. Florida Field Naturalist. 27(3). Aug., 1999. 121-123.
Meshaka, Walter E., Jr., 1999. The herpetofauna of the Kampong. Florida Scientist. 62(3-4). Summer-Autumn, 1999. 153-157.
Summary: Fourteen reptile and three amphibian species were present at the Kampong, a four ha tropical garden in Coconut Grove, Dade County, Florida. Only four species were native, indicating that the herpetofauna of the Kampong was an artifact assemblage dominated by exotic species, mostly small-bodied lizards. Eleven of the 13 exotic species present were established and comprised 42% of the terrestrial and arboreal exotic herpetofauna of Dade County. A new species for North America, Mabuya multifasciata (Lacertilia: Scincidae) of southeast Asia was recorded at the Kampong. The herpetofauna of the Kampong reflected the changing herpetofaunal community of southern Florida. The protected nature of the Kampong and recent acquisitions of adjacent land favor the persistence of both native and exotic herpetofauna.
Meshaka, Walter E., Jr; Ferster, Betty., 1995. Two species of snakes prey on Cuban treefrogs in southern Florida. Florida Field Naturalist. 23(4). 1995. 97-98.
Meshaka, Walter E., Jr; Jansen, Kevin P., Osteopilus septentrionalis (Cuban treefrog). Predation. Herpetological Review. 28(3). 1997. 147-148
Meshaka WE (1994) Ecological correlates of successful colonization in the life history of the Cuban Treefrog, Osteopilus septentrionalis (Anura: Hylidae). PhD Dissertation, Florida International University, Miami, Florida. pp. 55-69
NatureServe., 2008. Osteopilus septentrionalis - (Dum�ril and Bibron, 1841) Cuban Treefrog
Summary: Available from: http://www.natureserve.org/explorer/servlet/NatureServe?searchName=Osteopilus+septentrionalis [Accessed 4 September 2008]
Neils, Aletris; Bugbee, Chris., 2007. Rana catesbeiana (American Bullfrog). Diet. Herpetological Review. 38(4). DEC 2007. 443.
Owen, Jennifer; Perry, Gad; Lazell, James; Petrovic, Clive; Egelhoff, Jim., 2006. Osteopilus septentrionalis (Cuban tree frog). Colonization of the British Virgin Islands. Herpetological Review. 37(1). MAR 2006. 74-75.
Owen JL (2005) The Cuban tree frog (Osteopilus septentrionalis): distribution, diet, and reproduction of an invasive species in the British Virgin Islands (Doctoral dissertation, Texas Tech University).
Perry, Gad; Platenberg, Renata., 2007. Recent additions to the herpetofauna of little St. James, US Virgin Islands. Applied Herpetology. 4(4). 2007. 387-389.
Pieterson, E. Corrie; Addison, Lindsay M; Agobian, Jorge N; Brooks-Solveson, Brenda; Cassani, John; Everham, Edwin M. III., 2006. Five years of the Southwest Florida Frog Monitoring Network: Changes in frog communities as an indicator of landscape change. Florida Scientist. 69(Suppl. 2). 2006. 117-126.
Rice, Amanda N; Rice, Kenneth G; Waddle, J. Hardin; Mazzotti, Frank J., 2006. A portable non-invasive trapping array for sampling amphibians and reptiles. Herpetological Review. 37(4). DEC 2006. 429-430.
Rivero, J. A. 1998. Los anfibios y reptiles de Puerto Rico/The Amphibians and Reptiles of Puerto Rico. 2nd Ed. Edit. Univ. P. R. San Juan, P. R.
Summary: Introduction of the species in Puerto Rico
Salinas, Fernando Vargas., 2006a. Sexual size dimorphism in the Cuban treefrog Osteopilus septentrionalis. Amphibia-Reptilia. 27(3). SEP 2006. 419-426
Salinas, Fernando Vargas. 2006b. Breeding behavior and colonization success of the Cuban treefrog Osteopilus septentrionalis. Herpetologica. 62(4). DEC 2006. 398-408.
Smith, Kevin G., 2004. Osteopilus septentrionalis (Cuban treefrog). Reproductive behavior. Herpetological Review. 35(4). December 2004. 374-375.
Smith, Kevin G., 2005a. An exploratory assessment of Cuban Treefrog (Osteopilus septentrionalis) tadpoles as predators of native and nonindigenous tadpoles in Florida. Amphibia-Reptilia. 26(4). DEC 2005. 571-575.
Smith, Kevin G., 2005b. Effects of nonindigenous tadpoles on native tadpoles in Florida: evidence of competition. Biological Conservation. 123(4). JUN 05. 433-441.
Smith, Kevin G., 2006. Keystone predators (eastern newts, Notophthalmus viridescens) reduce the impacts of an aquatic invasive species. Oecologia (Berlin). 148(2). JUN 2006. 342-349.
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Contact
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MN
Osteopilus septentrionalis
rana cubana, rana platernera, Giant Tree-frog, Marbled Tree-toad, Cuban Treefrog
Date assessed
2021-03-26
Year published
2022
Eicat category
MN (Minor)
Justification for EICAT assessment


Osteopilus septentrionalis consume invertebrate and other prey (Smith 2005a; Owen 2005; Wyatt and Forys 2004; Meshaka 1994), and impact native species through competition, which affects the performance of the natives by inhibiting their growth and development as well as reducing their survivorship (Johnson 2007; Smith 2005b; Tennessen et al. 2014; 2016). They have also been shown to reduce the growth rate of snakes that eat them (Goetz et al. 2018).
Confidence rating
Low
Mechanism(s) of maximum impact
Predation; Poisoning/ toxicity; Competition
Countries of most severe impact
U.S.A.
Description of impacts

Predation - Osteopilus septentrionalis tadpoles are reported to reduce the survivorship of heterospecific tadpoles in shared ponds;
Poisoning/ toxicity - Osteopilus septentrionalis is toxic to native predators and predation on this invasive can result in the reduction of growth.; Competition - Osteopilus septentrionalis tadpoles inhibited the growth and development of native tadpoles. Adults alter acoustic environments and impacts acoustic behaviour of native amphibian species as well as masks the calls of natives
Assessor
Sabrina Kumschick; Nitya Prakash Mohanty; Corey Thorp; Carla Wagener
Contributors
John Measey; Mohlamatsane Mokhatla; James Baxter-Gilbert; Alexander D. Rebelo; Giovanni Vimercati; Sarah J. Davies; F. André de Villiers; Khensani Nkuna
Reviewers
EICAT authority
Recommended citation
Sabrina Kumschick, Nitya Prakash Mohanty, Corey Thorp, Carla Wagener (2024). Osteopilus septentrionalis. IUCN Environmental Impact Classification for Alien Taxa (EICAT).