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Hispaniolan Crossbill Loxia megaplaga



Justification

Justification of Red List category
This species has a very small, fragmented and declining range. Although its numbers fluctuate naturally, its available habitat is decreasing as a result of logging, small-scale agriculture and uncontrolled fires. It therefore qualifies as Endangered.

Population justification
The population is estimated to number 1,000-3,375 individuals following surveys in the Sierra de Baoruco between 1996-1999 (Latta et al. 2000, Hart 2020). This roughly equates to 750-2,300 mature individuals. Individual subpopulation sizes are unknown. It is tentatively assessed here that no subpopulation contains >250 mature individuals, but this may be an underestimate (see Hart 2020).

Trend justification
Numbers presumably declined between the mid-1920s and mid-1960s in response to habitat loss, but by 1978 the species was thought to be recovering (Woods and Ottenwalder 1986). Owing to agricultural encroachment into its habitat, the species is currently considered to be declining at a slow rate. Within the range, tree cover has been lost at a rate of 5% over the past ten years (Global Forest Watch 2020). Considering that the species is exclusively restricted to pine forest, population declines may be larger than the rate of tree cover loss, amounting to <10% over ten years. The population may additionally be fluctuating depending on food availability (Benkman 1994, Latta et al. 2000)

Distribution and population

Loxia megaplaga occurs primarily in Haiti and the Dominican Republic (Dod 1978, Clement et al. 1993). Several birds were found in the Blue Mountains of Jamaica in the early 1970s, but there have been no subsequent records (Dod 1978). In Haiti, the species is known from the Massifs de la Selle (Bond 1979) and de la Hotte (Woods and Ottenwalder 1986, Raffaele et al. 1998, Dávalos and Brooks 2001), including the Macaya Biosphere Reserve where small flocks were recorded in 2004 (Rimmer et al. 2005). In the Dominican Republic, it occurs mostly in the Sierra de Baoruco, with occasional records from the Cordillera Central (Smith 1997).

Ecology

The species is restricted to pine Pinus occidentalis forests, mostly at high elevations between 540 and 2,600 m (Benkman 1994, Latta et al. 2006). It feeds exclusively on pine-seeds (Woods and Ottenwalder 1986). Every three years, there is a large pine-cone crop, but crops in other years are small or fail altogether (Benkman 1994). Fluctuations in pine-cone abundance are not synchronous, and birds are nomadic in response to food availability. It breeds between January and April, with the timing probably depending on the cone crop (Latta et al. 2000, 2002). The nest is usually built high up in the branches of pine trees (Bond 1979, Latta et al. 2000).

Threats

Logging has been reduced since the mid-1960s, but clearance for small-scale agriculture continues to fragment remaining habitat (Dod 1978, Bond 1979, Woods and Ottenwalder 1986, Ottenwalder 1992). This presumably isolates populations, making them susceptible to local pine-cone failures (Benkman 1994). Habitat loss in the Sierra de Baoruco has recently accelerated owing to clearance for commercial-scale agriculture (S. Latta in litt. 2016). Parasitism by Shiny Cowbird Molothrus bonariensis may be a problem (Raffaele et al. 1998), but this seems unlikely since M. bonariensis is primarily a coastal species in the Sierra de Baoruco (Latta et al. 2000). The principal threat may now be uncontrolled stand replacement fires, which burn more of the remaining pine habitat than can be replaced through regeneration (Latta et al. 2000).

Conservation actions

Conservation Actions Underway
The vast majority of the population occurs in Sierra de Baoruco National Park, but there is no active protection of the park. Clearance for agriculture is widespread, especially in the border region (Clement et al. 1993, Latta et al. 2000). It has also been found in Armando Bermudez National Park in the Cordillera Central (D. C. Wege pers. obs. 1999) and Macaya Biosphere Reserve (Rimmer et al. 2005). A recovery plan was published in 1992 (Ottenwalder 1992).

Conservation Actions Proposed
Accurately determine the status and distribution of the species and its habitat (Ottenwalder 1992). Protect large tracts of mature pine forest over a range of elevations and geographic locations (Benkman 1994, Latta et al. 2000). Work with local communities to raise awareness and ensure the protection of the Sierra de Baoruco National Park.

Identification

15 cm. Medium-sized finch with distinctive crossed mandibles and two white wing-bars. Male pale red with black wings. Female dull olive with blackish wings, yellowish rump and breast, and fine dark streaking on breast. Voice High, emphatic chu-chu-chu-chu call. Also soft warble. Hints Best located by calls of small foraging groups. Regularly visits water to drink.

Acknowledgements

Text account compilers
Sharpe, C.J., Isherwood, I., Wheatley, H., Wege, D., Westrip, J.R.S., Hermes, C., Mahood, S., Pople, R.

Contributors
Latta, S. & Wege, D.


Recommended citation
BirdLife International (2024) Species factsheet: Hispaniolan Crossbill Loxia megaplaga. Downloaded from https://datazone.birdlife.org/species/factsheet/hispaniolan-crossbill-loxia-megaplaga on 23/12/2024.
Recommended citation for factsheets for more than one species: BirdLife International (2024) IUCN Red List for birds. Downloaded from https://datazone.birdlife.org/species/search on 23/12/2024.