IUCN Red List Criteria
| Critically Endangered |
|
| Endangered |
C2a(ii) |
| Vulnerable |
A2ac;B1ab(i,ii,iii,v);C2a(i,ii) |
IUCN Red List history
| Year |
Category |
| 2012 |
Endangered |
| 2011 |
Endangered |
| 2008 |
Vulnerable |
| 2006 |
Vulnerable |
| 2004 |
Vulnerable |
| 2000 |
Vulnerable |
| 1996 |
Vulnerable |
| 1994 |
Vulnerable |
| 1988 |
Threatened |
Species attributes
| Migratory status |
not a migrant |
Forest dependency |
High |
| Land mass type |
continent
|
Average mass |
442 g
|
Distribution
| |
Estimate |
Data quality |
| Extent of Occurrence breeding/resident (km2) |
1,300 |
medium |
| Extent of Occurrence non-breeding (km2) |
11,600 |
medium |
| Number of locations |
6-10 |
- |
| Fragmentation |
|
- |
Population & trend
| |
Estimate |
Data quality |
Derivation |
Year of estimate |
| No. of mature individuals |
1000-2499 |
medium |
Estimated |
2008 |
| Population trend |
Decreasing |
medium |
|
- |
| Number of subpopulations |
1 |
- |
- |
- |
| Largest subpopulation |
1000-2500 |
- |
- |
- |
| Generation length (yrs) |
11.1 |
- |
- |
- |
|
Population justification: The population was recently estimated at c.3,500 individuals; however, the species is thought to reach reproductive maturity at about four years of age (R. Valdés-Peña in litt. 2010), thus the number of mature individuals is conservatively estimated at fewer than 2,500 and placed in the band 1,000-2,499 mature individuals. |
|
Trend justification: The species's habitat suffered significant forest fires in 1998 and 2006, affecting one of the most important nesting colonies of the species, which used to hold c.44% of the breeding population in the late 1990s (R. Valdés-Peña et al. in litt. 2007). By 2007, this colony had declined by 75% compared to numbers in 1998. Data suggest that between 1999 and 2008, more than 15,400 ha of pine forests were destroyed in the species's breeding range, representing 11.9% of its Extent of Occurrence (1,300 km2) (S. G. Ortiz-Maciel et al. in litt. 2010). A general trend of declines in the numbers of nesting pairs has been noted in the rest of its known colonies (R. Valdés-Peña et al. in litt. 2007). Based on these data and observations, the species is suspected to have undergone a rapid decline during the last 33 years (estimate of three generations). |
Country/Territory distribution
| Country/Territory |
Occurrence status |
Extinct |
Breeding |
Non-breeding |
Passage |
| Mexico |
Native |
No |
|
|
|
Habitats & altitude
| Habitat (level 1) |
Habitat (level 2) |
Importance |
Occurrence |
| Forest |
Subtropical/Tropical Moist Montane |
major |
resident |
|
Altitude
|
2000 - 3500 m
|
Occasional altitudinal limits
|
1300 - 3700 m
|
Threats & impact
| Threat (level 1) |
Threat (level 2) |
Impact and Stresses |
| Agriculture & Aquaculture |
Annual & perennial non-timber crops / Small-holder farming |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Majority (50-90%) |
Slow, Significant Decline |
Medium Impact: |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
| Agriculture & Aquaculture |
Livestock farming & ranching / Small-holder grazing, ranching or farming |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Majority (50-90%) |
Slow, Significant Decline |
Medium Impact: |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
| Biological resource use |
Fishing & harvesting aquatic resources / Unintentional effects: (large scale) |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Minority (<50%) |
Slow, Significant Decline |
Low Impact: 5 |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
| Biological resource use |
Gathering terrestrial plants / Unintentional effects (species is not the target) |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Minority (<50%) |
Negligible declines |
Low Impact: 4 |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
| Biological resource use |
Hunting & trapping terrestrial animals / Intentional use (species is the target) |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Minority (<50%) |
Slow, Significant Decline |
Low Impact: 5 |
| Stresses |
| Species mortality |
|
| Natural system modifications |
Fire & fire suppression / Trend Unknown/Unrecorded |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Majority (50-90%) |
Slow, Significant Decline |
Medium Impact: |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
| Climate change & severe weather |
Droughts |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Majority (50-90%) |
Slow, Significant Decline |
Medium Impact: |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
Utilisation
| Purpose |
Primary form used |
Life stage used |
Source |
Scale |
Level |
Timing |
| Pets |
Whole |
Adults and juveniles |
Wild |
International |
Non-trivial |
Recent |
Recommended citation
BirdLife International (2013) Species factsheet: Rhynchopsitta terrisi. Downloaded from
http://www.birdlife.org on 19/06/2013.
Recommended citation for factsheets for more than one species: BirdLife International (2013) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 19/06/2013.
This information is based upon, and updates, the information published in BirdLife International (2000)
Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004)
Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.