|
|---|
Warning: Undefined property: stdClass::$Photo1 in /var/www/vhosts/virtualzoo/classifications/display.php on line 584
| Subspecies: | Unknown |
|---|---|
| Est. World Population: | |
| CITES Status: | NOT LISTED |
| IUCN Status: | Extinct in the Wild |
| U.S. ESA Status: | NOT LISTED |
| Body Length: | |
| Tail Length: | |
| Shoulder Height: | |
| Weight: | |
| Top Speed: | |
| Jumping Ability: | (Horizontal) |
| Life Span: | in the Wild |
| Life Span: | in Captivity |
| Sexual Maturity: | (Females) |
| Sexual Maturity: | (Males) |
| Litter Size: | |
| Gestation Period: | |
Habitat:
It was apparently commonest in forested areas above 500 m, dominated by Bumelia, Prunus serotina, Guettarda, Ilex, Psidium and Ficus. It was a highly terrestrial frugivore, and probably depended on an intact understorey of ferns and euphorbias.
Range:
This species has been extirpated from Socorro in the Revillagigedo Islands, Mexico. It was formerly common and observations in 1957 and 1958 gave no indication that it was declining. The last sighting in the wild was in 1972 (Baptista and Martínez-Gómez 1996), and all suitable habitat on the island has been surveyed subsequently without recording the dove (J. E. Martínez-Gómez in litt. 1999, 2000). Several individuals were taken during an expedition to the islands in 1925 and subsequently bred in the U.S.A., with some sent to Europe (Martínez-Gómez et al. 2003).
Conservation:
Conservation Actions Underway
The Revillagigedo Islands were declared a biosphere reserve in 1994 (Stattersfield et al. 1998, Martínez-Gómez et al. 2003). The European Association of Zoos and Aquaria recognised a breeding programme for the species, as initiated by Cologne and Frankfurt zoos (Germany) and the private interest group Wild Pigeons and Doves, as an official European Endangered species programme (EEP), in 1995 (Martínez-Gómez et al. 2003). Modern studbook software has been employed to assist with the genetic and demographic management of the captive population. Individuals have been distributed to zoos and bird parks in countries including Belgium, the Netherlands, U.K., Poland, Austria, Luxembourg, France, Spain, the Czech Republic and Germany (S. G. Stadler in litt. 2007, 2012). Of 672 individuals listed in the studbook by December 2010, 102 were known to be alive (S. G. Stadler in litt. 2012). Since 2006, following an extensive survey of the origin of the founding individuals of the EEP population, major software-based population genetic analyses have been conducted and recommendations for new pairs have been given by the EEP coordinator (S. G. Stadler in litt. 2007, 2012). A special breeding unit for the species has been opened at Marlow Bird Park, Germany (Martínez-Gómez et al. 2003). A proposal has been developed to reintroduce the species (Baptista and Martínez-Gómez 1996, Martínez-Gómez et al. 2003, S. G. Stadler in litt. 2012), along with a restoration programme for Socorro (Martínez-Gómez et al. 2003, Horblit et al. 2006). DNA fingerprinting has revealed extensive hybridisation with Z. macroura in the U.S.A., however it also showed a high degree of relatedness between the European population and pure individuals kept in California (Martínez-Gómez et al. 2003). As a result, the European population will be used for reintroduction efforts. The construction of breeding aviaries on Socorro began in August 2003 (Martínez-Gómez et al. 2003) and was completed by 2005 (Bell et al. 2005a). Resident populations of Z. macroura and Common Ground-dove Columbina passerina (Bell et al. 2005a) were screened in December 2003 and January 2004 to assess the presence of pathogens that might affect the reintroduction programme (Martínez-Gómez et al. 2003, Bell et al. 2005a, b). Avian malaria and trichomoniasis were detected in both species, and as a result recommendations were put forward (Bell et al. 2005a, b). In 2005, plans were outlined to control the locust outbreaks, restore native vegetation and assess the problem of erosion (J. E. Martínez-Gómez in litt. 2005). The arrival on Socorro of the first birds from the EEP was planned for June 2005 (Bell et al. 2005b), with the establishment of a breeding flock by June 2006 (Bell et al. 2005a, S. G. Stadler in litt. 2012). However, there have been problems with import restrictions and permits (J. E. Martínez-Gómez in litt. 2007). In the face of these restrictions a small insurance population was established in the U.S.A. in 2008 (H. Horblit in litt. 2007, J. E. Martínez-Gómez in litt. 2007), forming the basis for the return of the species to Africam Safari Zoo, Puebla, Mexico (S. G. Stadler in litt. 2012). Two groups of birds were transferred to Mexico in 2013 and 2014 to form the basis of a population for eventual reintroduction to Socorro (J. E. Martínez-Gómez in litt. 2016). Control of feral cats has been undertaken on Socorro ( B. Tershy in litt. 1999) although despite over over five hundred cats being killed on the island between 2011-2016, they still persist throughout the island in low numbers (B. Tershy in litt. 2007, J. E. Martínez-Gómez in litt. 2016, Ortíz-Alcaraz et al. 2017, Lowen 2020). Furthermore, over 1,700 feral sheep were culled on the island between 2009-2012 (Ortíz-Alcaraz et al. 2016) and as of 2012, sheep were completely eradicated from the island, facilitating a rapid, remarkable recovery in local vegetation cover (Ortíz-Alcaraz et al. 2017, Lowen 2020). Reports that rats have recently colonised Socorro have proved to be unfounded (J. E. Martínez-Gómez in litt. 1999, 2000) although mice remain an issue on the island and must be removed due to their predation of dove chicks (J. Lowen in litt. 2020). Techniques to grow four endemic tree species from Socorro have been successful, with 117 tree seedlings planted on the island. These restored areas will be important when birds are eventually released back onto Socorro (J. E. Martínez-Gómez in litt. 2016). The species is included on the 'Watch List' of the State of North America's Birds as a species of high conservation concern (NABCI 2016).Conservation Actions Proposed
Import birds from the EEP and establish a breeding flock on Socorro (Bell et al. 2005a, b, J. E. Martínez-Gómez in litt. 2007, S. G. Stadler in litt. 2012). Complete the eradication of cats and sheep on Socorro (J. E. Martínez-Gómez in litt. 2005, 2007). Continue to restore native vegetation on Socorro (J. E. Martínez-Gómez in litt. 2005). Reintroduce the species following satisfactory progress in mammal eradication (J. E. Martínez-Gómez in litt. 2005, 2007) and habitat restoration programmes (Martínez-Gómez et al. 2003, Horblit et al. 2006, J. E. Martínez-Gómez in litt. 2005). Put measures in place to control, but not eliminate, the locust swarm (J. E. Martínez-Gómez in litt. 2005, Song et al. 2006).
The Revillagigedo Islands were declared a biosphere reserve in 1994 (Stattersfield et al. 1998, Martínez-Gómez et al. 2003). The European Association of Zoos and Aquaria recognised a breeding programme for the species, as initiated by Cologne and Frankfurt zoos (Germany) and the private interest group Wild Pigeons and Doves, as an official European Endangered species programme (EEP), in 1995 (Martínez-Gómez et al. 2003). Modern studbook software has been employed to assist with the genetic and demographic management of the captive population. Individuals have been distributed to zoos and bird parks in countries including Belgium, the Netherlands, U.K., Poland, Austria, Luxembourg, France, Spain, the Czech Republic and Germany (S. G. Stadler in litt. 2007, 2012). Of 672 individuals listed in the studbook by December 2010, 102 were known to be alive (S. G. Stadler in litt. 2012). Since 2006, following an extensive survey of the origin of the founding individuals of the EEP population, major software-based population genetic analyses have been conducted and recommendations for new pairs have been given by the EEP coordinator (S. G. Stadler in litt. 2007, 2012). A special breeding unit for the species has been opened at Marlow Bird Park, Germany (Martínez-Gómez et al. 2003). A proposal has been developed to reintroduce the species (Baptista and Martínez-Gómez 1996, Martínez-Gómez et al. 2003, S. G. Stadler in litt. 2012), along with a restoration programme for Socorro (Martínez-Gómez et al. 2003, Horblit et al. 2006). DNA fingerprinting has revealed extensive hybridisation with Z. macroura in the U.S.A., however it also showed a high degree of relatedness between the European population and pure individuals kept in California (Martínez-Gómez et al. 2003). As a result, the European population will be used for reintroduction efforts. The construction of breeding aviaries on Socorro began in August 2003 (Martínez-Gómez et al. 2003) and was completed by 2005 (Bell et al. 2005a). Resident populations of Z. macroura and Common Ground-dove Columbina passerina (Bell et al. 2005a) were screened in December 2003 and January 2004 to assess the presence of pathogens that might affect the reintroduction programme (Martínez-Gómez et al. 2003, Bell et al. 2005a, b). Avian malaria and trichomoniasis were detected in both species, and as a result recommendations were put forward (Bell et al. 2005a, b). In 2005, plans were outlined to control the locust outbreaks, restore native vegetation and assess the problem of erosion (J. E. Martínez-Gómez in litt. 2005). The arrival on Socorro of the first birds from the EEP was planned for June 2005 (Bell et al. 2005b), with the establishment of a breeding flock by June 2006 (Bell et al. 2005a, S. G. Stadler in litt. 2012). However, there have been problems with import restrictions and permits (J. E. Martínez-Gómez in litt. 2007). In the face of these restrictions a small insurance population was established in the U.S.A. in 2008 (H. Horblit in litt. 2007, J. E. Martínez-Gómez in litt. 2007), forming the basis for the return of the species to Africam Safari Zoo, Puebla, Mexico (S. G. Stadler in litt. 2012). Two groups of birds were transferred to Mexico in 2013 and 2014 to form the basis of a population for eventual reintroduction to Socorro (J. E. Martínez-Gómez in litt. 2016). Control of feral cats has been undertaken on Socorro ( B. Tershy in litt. 1999) although despite over over five hundred cats being killed on the island between 2011-2016, they still persist throughout the island in low numbers (B. Tershy in litt. 2007, J. E. Martínez-Gómez in litt. 2016, Ortíz-Alcaraz et al. 2017, Lowen 2020). Furthermore, over 1,700 feral sheep were culled on the island between 2009-2012 (Ortíz-Alcaraz et al. 2016) and as of 2012, sheep were completely eradicated from the island, facilitating a rapid, remarkable recovery in local vegetation cover (Ortíz-Alcaraz et al. 2017, Lowen 2020). Reports that rats have recently colonised Socorro have proved to be unfounded (J. E. Martínez-Gómez in litt. 1999, 2000) although mice remain an issue on the island and must be removed due to their predation of dove chicks (J. Lowen in litt. 2020). Techniques to grow four endemic tree species from Socorro have been successful, with 117 tree seedlings planted on the island. These restored areas will be important when birds are eventually released back onto Socorro (J. E. Martínez-Gómez in litt. 2016). The species is included on the 'Watch List' of the State of North America's Birds as a species of high conservation concern (NABCI 2016).Conservation Actions Proposed
Import birds from the EEP and establish a breeding flock on Socorro (Bell et al. 2005a, b, J. E. Martínez-Gómez in litt. 2007, S. G. Stadler in litt. 2012). Complete the eradication of cats and sheep on Socorro (J. E. Martínez-Gómez in litt. 2005, 2007). Continue to restore native vegetation on Socorro (J. E. Martínez-Gómez in litt. 2005). Reintroduce the species following satisfactory progress in mammal eradication (J. E. Martínez-Gómez in litt. 2005, 2007) and habitat restoration programmes (Martínez-Gómez et al. 2003, Horblit et al. 2006, J. E. Martínez-Gómez in litt. 2005). Put measures in place to control, but not eliminate, the locust swarm (J. E. Martínez-Gómez in litt. 2005, Song et al. 2006).




