Ontologia
Phoenix theophrasti

Phoenix theophrasti

Greuter

NTLR Monde (IUCN)
1 photo · Licences CC (Wikimedia Commons / iNaturalist)Click pour agrandir

Description

phoenix theophrasti.

Source : Wikidata

Pays · région · aire protégée · écorégion · biome

Graphe en cours d’indexation

Calcul du tissu écologique de Phoenix theophrasti.

Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).

Liste rouge IUCN

NT · Quasi menacéecritères B2b(v)Stable
Évaluation complète
Évaluation
2017 · v3.1
Altitude
0250 m
Profondeur
m
État de la populationExpert
The population size on Crete exceeds 6,500 individuals; the largest being at 'Palm beach' at Vai in eastern Crete. The overall population trend is considered to be stable (EEA 2012).

Menaces identifiées(6 menaces classées CMP-IUCN)

  • 7_1_3
    Trend Unknown/Unrecorded
    Causing/Could cause fluctuationsMinority (<50%)Ongoing
  • 1_3
    Tourism & recreation areas
    UnknownMinority (<50%)Ongoing
  • 7_2_8
    Abstraction of ground water (unknown use)
    UnknownUnknownOngoing
  • 8_1_2
    Named species
    UnknownMajority (50-90%)Ongoing
  • 8_1_2
    Named species
    Slow, Significant DeclinesUnknownFuture
  • 8_1_2
    Named species
    Slow, Significant DeclinesUnknownFuture
Description complète des menacesExpert
Since this species depends on large amounts of available freshwater for its survival, drainage activities and water pollution pose a serious threat.

Further threats include (L. Stephenson pers. comm. 2016);
1. Red Palm Weevil Rhynchophorus ferrugineus Oliv. (Dembilio et al. 2011). This pest severely impacted Phoenix canariensis on the Canaries, and whilst the weevil has currently been eradicated from the Canaries after significant effort, the eradication of the weevil once established would be difficult. Whilst at present the Red Palm Weevil has only severely impacted non-native palms planted in Crete (EEA 2012), the Red Palm Weevil has been observed to infest young plants of P. theophrasti up to five years old in cultivation at the MAICh Botanical Garden, suggesting that there is the potential for the recruitment of P. theophrasti to be impacted in the wild.
2. Hybridisation with Phoenix canariensis which are popular garden and street trees in all tourist areas: the extent and impact of this threat requires further research.
3. Tourist development, especially in the area of the largest forest existing at Va on Crete.
4. Water extraction for agriculture (and any future tourist development) in the same area.
5. The invasive South American Palm Borer (Paysandisia archon) has been reported from Crete and is another potentially significant threat to this palm (Niamouris and Psirofonia 2012), and has been found to have infected P. canariensis palms cultivated in Spain and imported to the UK (Reid and Moran 2009).

Fires also impact the species, however the plant regenerates well post-fire.

Habitats préférentiels (classification IUCN)

  • 1_4Forest - Temperate
  • 5_1Wetlands (inland) - Permanent Rivers/Streams/Creeks (includes waterfalls)
  • 5_2Wetlands (inland) - Seasonal/Intermittent/Irregular Rivers/Streams/Creeks
Mesures de conservation recommandéesExpert
The largest subpopulation is protected under Greek law (Presidential Decree 67/81), and it has been assessed as Vulnerable on Crete (Phitos et al. 1995, 2009).

'Palm groves of Phoenix' is an Annex I habitat type of the Habitats Directive (EUNIS 2015) and is considered as a priority for conservation. The species is protected under Annex I of the Bern Convention, and is included in the Annexes II and IV of the Habitats Directive. In 1973, the population at Vai was declared an 'Aesthetic Forest Preserve' (P.D. 121/73, FEK 170/A΄/73) and is now protected by national legislation. The species is recorded as occurring in ten Natura 2000 sites in Greece (EUNIS 2015). The palm is listed in 70 ex situ collections (BGCI 2016). The species was a focus of the Monitoring and evaluation of the Conservation Status of Plant Species of Annexes II and IV of the 92/43/EEC Directive in Greece project (2014-2015).
Stress écologiques (8)Expert
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_3_1Hybridisation
Usage & commerce (1)Expert
  • 13Pets/display animals, horticulture
    internationalnationalsubsistance
Priorités de recherche (4)Expert
  • 1_1Taxonomy
  • 1_2Population size, distribution & trends
  • 1_5Threats
  • 3_1Population trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Palearctic

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Tree - size unknown
Références bibliographiques (19)Expert
  1. IUCN. 2019. The IUCN Red List of Threatened Species. Version 2019-3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 10 December 2019).
  2. IUCN. 2017. The IUCN Red List of Threatened Species. Version 2017-3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 5 December 2017).
  3. Strid, A. 2016. Atlas of the Aegean Flora. <i>Englera</i> 33(1): 1-1578.
  4. BGCI. 2016. PlantSearch. London: Botanic Gardens Conservation International Available at: <a href="www.bgci.org/plant_search.php">www.bgci.org/plant_search.php</a>.
  5. Tsakiri, M., Kougioumoutzis, K. and Iatrou, G. 2016. Contribution to the vascular flora of Chalki Island (East Aegean, Greece) and biomonitoring of a local endemic taxon. <i>Willdenowia</i> 46(1): 175-190.
  6. WCSP. 2015. World Checklist of Selected Plant Families. Available at: <a href="http://apps.kew.org/wcsp/">http://apps.kew.org/wcsp/</a>.
  7. EUNIS. 2015. Biodiversity Database. Available at: <a href="http://eunis.eea.europa.eu/">http://eunis.eea.europa.eu/</a>. (Accessed: 2014).
  8. Bakış, Y., Babaç, M.T. and Uslu, E. 2014. Turkish Plants Data Service (TÜBİVES). Available at: <a href="http://www.tubives.com/index.php">http://www.tubives.com/index.php</a>. (Accessed: January 2016).
  9. Rivera, D., Obón, C., García-Arteaga, J., Egea, T., Alcaraz, F., Laguna, E., Carreño, E., Johnson, D., Krueger, R., Delgadillo, J. and Ríos, S. 2014. Carpological analysis of <i>Phoenix</i> (Arecaceae): Contributions to the taxonomy and evolutionary history of the genus. <i>Botanical Journal of the Linnean Society</i> 175: 74-122. doi:10.1111/boj.12164.
  10. Ballardini, M., Mercuri, A., Littardi, C., Abbas, S., Couderc, M., Ludeña, B. and Pintaud, J.-C. 2013. The chloroplast DNA locus psbZ-trnfM as a potential barcode marker in <i>Phoenix</i> L. (Arecaceae). <i>ZooKeys </i> 365: 71-82. doi: 10.3897/zookeys.365.5725.
  11. EAA. 2012. Report under the Article 17 of the Habitats Directive Period 2007-2012: <i>Phoenix theophrasti</i>. European Environment Agency.
  12. Niamouris, K. and Psirofonia, P. 2012. First report of <i>Paysandisia archon</i> on <i>Phoenix theophrasti</i>. <i>Entomologia Hellenica</i> 21: 74-76.
  13. Dembilio, O., Karamaouna, F., Kontodimas, D.C., Nomikou, M. and Jacas, J.A. 2011. Short communication. Susceptibility of <i>Phoenix theophrasti</i> (Palmae: Coryphoideae) to <i>Rhynchophorus ferrugineus</i> (Coleoptera: Curculionidae) and its control using <i>Steinernema carpocapsae</i> in a chitosan formulation. <i>Spanish Journal of Agricultural Research</i> 9(2): 623-626.
  14. Pintaud, J.C., Zehdi, S., Couvreur, T., Barrow, S., Henderson., S., Aberlenc-Bertosi, F., Tregear, J.W., Billotte, N. 2010. Species delimitation in the genus <i>Phoenix</i> (Arecaceae) based on SSR markers, with emphasis on the identity of the date palm (<i>Phoenix dactylifera</i> L. In: O. Seberg, G. Petersen, A. Barfod and J. Davis (eds), <i>Diversity, phylogeny, and evolution in the monocotyledons</i>, pp. 267–286. Aarhus University Press, Aarhus.
  15. Phitos, D., Constantinidis, T. and Kamari, G. (eds). 2009. <i>The Red Data Book of Rare and Threatened Plants of Greece. Volume One (A-D)</i>. Hellenic Botanical Society, Patras.
  16. Reid, S. and Moran, H. 2009. Palm borer <i>Paysandisia archon</i>. Plant Pest Factsheet. Department for Environment Food and Rural Affairs, London.
  17. Phitos, D., Constantinidis, T. and Kamari, G. (eds). 2009. <i>The Red Data Book of Rare and Threatened Plants of Greece. Volume Two (E-Z)</i>. Hellenic Botanical Society, Patras.
  18. Barrow, S.C. 1998. A Monograph of <i>Phoenix</i> L. (Palmae: Coryphoideae). <i>Kew Bulletin</i> 53(3): 513-575.
  19. Phitos, D., Strid, A., Snogerup, S. and Greuter, W. (eds). 1995. <i>The Red Data Book of Rare and Threatened Plants of Greece.</i> WWF-Greece, Athens.
Évaluateurs & contributeurs (3)Expert
assessor
Allen, D.J.
contributor
Strid, A., Bazos, I., Fournaraki, C., Göçmen Taşkın, B. & Delipetrou, P.
evaluator
Bazos, I., Fournaraki, C., Delipetrou, P. & Gardiner, L.M.
1 erratum publié après l'évaluation.

Allen, D.J. 2017. Phoenix theophrasti (Europe assessment) (errata version published in 2019). The IUCN Red List of Threatened Species 2017: e.T38630A155586274. Accessed on 05 May 2026.

Indicateurs écologiques

Indicateurs écologiques Ellenberg-type

EIVE 1.0 — Dengler 2023

Position de l'espèce sur les 5 dimensions écologiques européennes (M / N / R / L / T), échelle 0-10. La zone estompée représente la niche width (variabilité tolérée).

MNRLT
Humidité
xérophile hygrophile
6.1
hygrophile
Azote
oligotrophe nitrophile
7.1
nitrophile
Réaction (pH)
silicicole calcicole
8.4
calcicole strict
Lumière
sciaphile héliophile
7.5
héliophile
Température
cryophile thermophile
8.5
thermophile strict

Source : EIVE 1.0 (Dengler et al. 2023). CC-BY 4.0. Échelle harmonisée 0-10 (équivalent inverse-rang sur les systèmes Ellenberg, Landolt, Pignatti, etc.). Niche width = écart-type d'estimation, indicateur de fiabilité (zone estompée).

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

Consulter sur les bases externes

Observations & statuts

Cartographie

Bibliographie