







| Kingdom | Phylum | Class | Order | Family |
|---|---|---|---|---|
| ANIMALIA | CHORDATA | AVES | Galliformes | Odontophoridae |
| Scientific Name: | Colinus virginianus | |||
| Species Authority: | (Linnaeus, 1758) | |||
Common Name/s:
|
||||
| Taxonomic Notes: | Colinus virginianus (Sibley and Monroe 1990, 1993) was provisionally split into C. virginianus and C. ridgwayi by Stotz et al. (1996) but this treatment has not been adopted, following SACC (2005). | |||
| Red List Category & Criteria: | Near Threatened ver 3.1 | ||||||||||||
| Year Assessed: | 2008 | ||||||||||||
| Assessor/s | BirdLife International | ||||||||||||
| Evaluator/s: | Bird, J. & Butchart, S. (BirdLife International Red List Authority) | ||||||||||||
|
Justification: This species qualifies as Near Threatened because it has suffered moderately rapid declines in recent decades becoming rarer in many traditional strongholds owing to habitat conversion. |
|||||||||||||
| History: |
|
||||||||||||
| Population: |
Rich et al. (2004)
|
| Population Trend: |
Decreasing
|
| Habitat and Ecology: | It is found in early successional vegetation in a variety of habitats, created by disturbances from fire, agriculture and timber-harvesting1. It is principally a seed feeder but insects form an important component of the diet in summer3. It forms coveys of 8-20 birds occupying a home range of approximately 10 ha. |
| Systems: | Terrestrial |
| Major Threat(s): | Changes in agricultural land use (weed removal and herbicide use), forestry (high-density pine plantations), and lack of use of prescribed fire have resulted in widespread habitat fragmentation1. Over 20,000,000 individuals were recently being killed annually by hunters in the USA3; poor management of populations could result in declines. |
| Conservation Actions: |
Conservation actions underway: Subspecies ridgwayi is on CITES Appendix I3. Restoration efforts are attempting to conserve this population in Arizona3. Conservation actions proposed: Frequent vegetation disturbance (every 1-5 yr) from prescribed fire and/or mechanical disturbances is essential for maintaining abundant populations in forest habitats. Maintaining tree canopy cover at <50% to create open, parklike conditions is essential. Burn 50-75% of understory vegetation annually during late winter to early summer, in small, patchy mosaics. Research needs to be done in order to understand how to mitigate potential additive effects of hunting mortality (e.g. experiments that examine population productivity and recovery at various harvest regimes and densities). Optimal timing of prescribed fire for habitat management needs to be determined from field research and experimentation. Removal and reduction of mammalian predators during nesting may be useful if also conducted within the context of intensive habitat management. Improve understanding of the Mexican populations. |
| Citation: | BirdLife International 2008. Colinus virginianus. In: IUCN 2009. IUCN Red List of Threatened Species. Version 2009.2. <www.iucnredlist.org>. Downloaded on 09 February 2010. |
| Disclaimer: | To make use of this information, please check the <Terms of Use>. |
| Feedback: | If you see any errors or have any questions or suggestions on what is shown on this page, please fill in the feedback form so that we can correct or extend the information provided |