Ontologia

Costus barbatus

Suess.

CRLR Monde (IUCN)
Pays · région · aire protégée · écorégion · biome

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Calcul du tissu écologique de Costus barbatus.

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Liste rouge IUCN

CR · En danger critiquecritères A2c; C2a(i,ii); DDécroissante
Évaluation complète
Évaluation
2014 · v3.1
Altitude
12001800 m
Profondeur
m
État de la populationExpert
In 2011, this assessor made a concerted effort to locate this species in its natural habitat in the eastern suburbs of San Jose, Costa Rica. Using Google Earth, remaining patches of forest at the appropriate altitudes were identified, then visited. All forest patches within the known altitude range of this species were found to be reclaimed coffee fields and no species of Costaceae whatsoever were found in these areas. As noted in the distribution section, this assessor found one very small subpopulation (one clump) of this species in a small creek bed about 5 km east of the known collections and at a higher altitude (1,780 metres) than this species was previously known to exist. This was a large clump with plants at varying levels of maturity from non-flowering plants, to young inflorescences, and including mature inflorescences which normally would contain seeds. No seeds or seedlings were found whatsoever, so it is believed that either the pollinator is extinct or not found at that elevation, or the plant does not maintain sufficient numbers to recruit a pollinator.

Prior to this, the most recent creditable collection record was in 1994 at Parque Nacional Tapanti. This assessor visited the area and the same trail noted in the collection record in 2006 and Costus barbatus was not found there. The other two collection records there were in 1978 and 1974. 

The next prior collection was in 1984, in an area very close to the 2011 observation, to the east of San Jose.

The third area (southwest of San Jose) had one collection record in 1994, and has not been verified by this assessor.

It is difficult to estimate the number of plants still in existence in the wild, but based on the recorded collection data and the many areas searched by this assessor, the number must be very low. Current population size is estimated at  under 50 mature plants.

Menaces identifiées(3 menaces classées CMP-IUCN)

  • 1_1
    Housing & urban areas
    Rapid DeclinesMajority (50-90%)Ongoing
  • 2_1_3
    Agro-industry farming
    Rapid DeclinesMajority (50-90%)Ongoing
  • 2_3_4
    Scale Unknown/Unrecorded
    Rapid DeclinesMajority (50-90%)Ongoing
Description complète des menacesExpert
The primary threat has been habitat loss in the past, and the few remaining subpopulations (if they exist) continue to be under that threat. The one area where this species was recently found has mostly been converted to pasture land and there is no protected status known that would prevent further loss of habitat in that area.  The other area where this species is believed to exist (above the Orosi valley) has mostly been converted to coffee growing.

Furthermore, the one subpopulation where this species was found recently, all the plants were sterile although they were mature enough that normally would be producing seeds. It is therefore believed that the pollinator is either extinct or at lower altitudes, or the small population was unable to recruit pollinators.

Habitats préférentiels (classification IUCN)

  • 1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesExpert
Currently there is no active in situ or ex situ conservation activity for this species.  Conservation efforts may be confused by the popular use of Costus comosus as an ornamental plant, incorrectly named as this species. The true species Costus barbatus should be collected and conserved in botanical gardens. A more detailed survey of the Tapantí National Park should be conducted and if this species is not found there or found as expected in very limited numbers, it should be reintroduced there in a dedicated area where it can be monitored.
Actions de conservation (3)Expert
  • 3_3_1Reintroduction
  • 3_4_1Captive breeding/artificial propagation
  • 3_4_2Genome resource bank
Stress écologiques (7)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
Priorités de recherche (3)Expert
  • 2_1Species Action/Recovery Plan
  • 2_2Area-based Management Plan
  • 3_4Habitat trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Neotropical

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Geophyte
Références bibliographiques (5)Expert
  1. Instituto Nacional de Biodiversidad, Costa Rica. 2016. Collection records. Santo Domingo de Heredia, Costa Rica Available at: <a href="http://www.inbio.ac.cr">http://www.inbio.ac.cr</a>. (Accessed: September 2016).
  2. IUCN. 2014. The IUCN Red List of Threatened Species. Version 2014.1. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 12 June 2014).
  3. Skinner, D. 2011. Will the real <i>Costus barbatus</i> please stand up! <i>Heliconia Society International Quarterly Bulletin</i> 17(4): 11-14.
  4. Maas, P.J.M. 1977. <i>Flora Neotropica Monograph No. 18 Renealmia (Zingiberaceae - Zingiberoideae), Costoideae (Additions) (Zingiberaceae)</i>. New York Botanical Garden, New York.
  5. Maas, P.J.M. 1972. <i>Flora Neotropica Monograph No. 8, Costoideae (Zingiberaceae)</i>. Hafner Publishing Company, Inc., New York.
Évaluateurs & contributeurs (2)Expert
assessor
Skinner, D.
evaluator
Magos Brehm, J.

Skinner, D. 2014. Costus barbatus. The IUCN Red List of Threatened Species 2014: e.T56234708A56234711. Accessed on 05 May 2026.

Répartition mondiale (heatmap GBIF)Construction en cours

0 obs · 0 cellules
Construction par partitions temporelles GBIF0%

Source : GBIF — observations agrégées par hexagones 0.2° × 0.2° (~22km). Filtre qualité : précision coordonnée < 10 km. Coloration quantile (q50/70/90/99). Fond carte : OpenFreeMap · © OpenStreetMap.

Distribution mondiale

Calcul de la distribution GBIF· ~10–60 s

Phénologie

Calcul du calendrier d'apparition· ~5–30 s

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