Ontologia
Loutre de mer

Loutre de mer

Lontra felina(Molina, 1782)

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

Description

espèce de mammifères carnivores

Source : Wikidata

Pays · région · aire protégée · écorégion · biome
Chargement du graphe…

Indicateurs du réseau écologique

Comment lire ce graphe

Ce graphe représente les interactions écologiques documentées entre Lontra felina et d'autres espèces, à partir de la base GloBI (Global Biotic Interactions, agrégation mondiale de la littérature scientifique) — source principale, complétée par d'autres jeux de données d'interactions agrégés par Ontologia. Il faut le comprendre comme une carte du savoir documenté, pas une carte de la réalité écologique exhaustive.

Limites principales

  • Incomplet. La majorité des interactions écologiques en milieu naturel n'ont jamais été publiées. Une espèce sans liens visibles n'est pas isolée — elle est probablement mal étudiée.
  • Biais publication pharmaco-agronomique. La littérature des interactions est polarisée par les enjeux économiques et sanitaires : parasitism / pathogen sur-pondéré sur les mammifères (recherche zoonoses, vecteurs), herbivory sur-pondéré sur les insectes phytophages (entomologie agronomique). À l'inverse, mutualisms, commensalisms et interactions sol/microbiote sont sous-cités. Conseil de lecture : sur les hubs mammifères ou les insectes ravageurs de culture, lire les arêtes parasitism / herbivory dominantes relativement au contexte de littérature, pas comme une mesure d'intensité écologique brute. Détails §10.1.
  • Biaisé vers les espèces étudiées. Quelques espèces (oiseaux communs, abeille mellifère, espèces modèles) concentrent disproportionnellement plus d'interactions documentées. Notre score composite ajoute un malus aux hubs de littérature pour atténuer cette dominance visuelle.
  • Interactions documentées globalement. Toutes les espèces affichées sont observées en France métropolitaine (les observations sont filtrées sur le territoire métropolitain), mais les interactions entre elles proviennent de la littérature scientifique mondiale. Une interaction documentée à l'étranger peut ne pas se réaliser à l'identique sur votre territoire. Le filtre « restreindre à ma commune » tient compte de la co-occurrence spatiale locale mais ne garantit pas l'interaction effective.
  • Sans dimension temporelle. Les variations saisonnières (migration, floraison, cycle de vie) ne sont pas modélisées.
  • Force d'interaction approximative. L'épaisseur des liens reflète le nombre de fois où l'interaction a été rapportée dans la littérature, pas son importance écologique réelle.

Comment nous sélectionnons les espèces affichées

Le graphe affiche au plus 31 nœuds par fiche (1 centre + 15 bulles depth=1 + 15 partenaires depth=2). Le serveur sélectionne intelligemment :

  • Bulles famille créées si une cascade taxonomique existe ou si ≥3 espèces directement documentées partagent une même famille — les espèces sont absorbées dans la bulle (pas de doublon visuel)
  • Espèces individuelles uniquement quand <3 dans une famille (sans cascade) — relations directes documentées
  • Pas d'espèces inférées affichées en doublon — les cascades sont représentées via les bulles famille uniquement
  • Partenaires depth=2 sélectionnés via algo priorité : candidat partagé par ≥2 docs de la famille (food web central) → reliant entre bulles → top sum_obs en dernier recours
  • Sous-types GloBI traduits en français au survol de la flèche (chasse, parasite, parasitoïde, mycorhize…)

Le toggle Profondeur 1 ↔ 2 client-side cache ou affiche les partenaires depth=2 sans refetch. Filtres règne, type d'interaction, ordres/familles, patrimoniales et commune recalculent côté serveur (slow path live ~1-2 s).

Indicateurs avancés (mode expert) : Modularité Q (Newman 2006, PNAS), communautés (Louvain, Blondel et al. 2008, J. Stat. Mech.), nestedness NODF (Almeida-Neto et al. 2008, Oikos).

Source : GloBI · TAXREF v18 (INPN/MNHN) · BDC-Statuts · Wikidata

37 partenaires écologiques documentés directement dans GloBI.

Partenaires
37
Espèces avec interactions documentées
Types d'interactions
4
Prédation, pollinisation, parasitisme…
Connectance
0.066
Densité des liens dans le sous-graphe affiché
Rang animalia
91 %
Percentile vs ensemble des animalia

Liste rouge IUCN

EN · En dangercritères A4ceDécroissante
Évaluation complète
Évaluation
2022 · v3.1
Altitude
01994 m
Profondeur
500 m
État de la populationExpert
The density estimates proposed by various authors are variable (from 0.04 to 10 individuals per kilometre, see Castilla and Bahamondes 1979, Castilla 1982, Cabello 1983, Rozzi and Torres-Mura 1990, Ebensberger and Castilla 1991, Sanchez 1992, Sielfeld 1992, Medina 1995, Apaza et al. 2004, Mangel and Alfaro-Shigueto 2004, Medina-Vogel et al. 2006), therefore the reported numbers are to be considered with care. Survey numbers and abundance estimations are highly dependent on the methodology applied (Valqui 2012) and detecting individuals at the rocky shores is exceedingly difficult. The fact that the species is solitary or present only in small groups (not larger than ten individuals) makes it difficult to determine if the species is abundant in one specific area. Nevertheless, a total population of about 800 to 2,000 individuals is proposed for the Peruvian coast (ca 150 km) by Valqui (2012). For Chile, it has been described that a length of ​​coastline close to 4,700 km is suitable for the Marine Otter (Sielfeld and Castilla 1999), however, the most recent density studies were carried out more than 30 years ago, so defining the current population of this species, with such dated data, may poorly reflect current status or trends. There are no population data from continental populations of Peru or from Argentina.

Menaces identifiées(23 menaces classées CMP-IUCN)

  • 1_3
    Tourism & recreation areas
    Causing/Could cause fluctuationsMinority (<50%)Ongoing
  • 3_3
    Renewable energy
    Causing/Could cause fluctuationsMinority (<50%)Ongoing
  • 4_3
    Shipping lanes
    Causing/Could cause fluctuationsMinority (<50%)Ongoing
  • 7_2_11
    Dams (size unknown)
    Causing/Could cause fluctuationsMinority (<50%)Ongoing
  • 5_1_1
    Intentional use (species is the target)
    Negligible declinesMinority (<50%)Ongoing
  • 5_1_3
    Persecution/control
    Negligible declinesMinority (<50%)Ongoing
  • 6_1
    Recreational activities
    Negligible declinesMinority (<50%)Ongoing
  • 6_3
    Work & other activities
    Negligible declinesMinority (<50%)Ongoing
  • 9_1_1
    Sewage
    Negligible declinesMajority (50-90%)Ongoing
  • 9_1_2
    Run-off
    Negligible declinesMajority (50-90%)Ongoing

+ 13 menaces supplémentaires

Description complète des menacesExpert
The major threats derive from an intensive urbanization of western South America, where the immense anthropogenic pressure on the coastal ecosystem is leading to accelerated habitat degradation and increased fragmentation (Brownell 1978, Eisenberg and Redford 1989, Sielfield and Castilla 1999, Medina-Vogel et al. 2008, Vianna et al. 2010). Urban development conflicts with the Marine Otter’s use of the coastline. It is not yet clear at what point these fragmentation forces will cause isolation to result in local extinction events due to lack of gene flow (Valqui 2012). In any case, these global changes will trigger more specific local threats in different regions.

Human-otter coexistence must acknowledge competition for resources that humans exploit for food, commerce and housing (Moreno et al. 1984; Ostfeld et al. 1989; Moreno 2001; Medina-Vogel et al. 2004, 2007, 2008). Industrial and artisan fishing ports have been established along the Pacific coast, affecting structure and productivity of marine life communities. Although Lontra felina shows certain capacity to coexist with humans, for example in fishing ports (Valqui 2004, Ruiz 2009, Medina-Vogel et al. 2007, Mangel et al. 2010), fishing has intensified global natural declines in the abundance of many forage fishes, leading to reduced reproductive success and reduced abundance of many birds and marine mammals (Majluf et al. 2002). Additionally, Marine Otters may be persecuted and killed directly for alleged damage to local fish, bivalves, and shrimp populations (Miller et al. 1983, Redford and Eisenberg 1992, Apaza et al. 2004). The species' preference for coastal waters that offer an abundance and diversity of prey conflicts with growing small-scale fisheries. Small-scale fishermen increased 34% from 1995 to 2005, and fishing boats 54% within the same decade (Alfaro-Shigueto et al. 2010). Although there is no qualitative documentation of bycatch, there are an increasing number of reports of Marine Otters entangled and drowned in fishing nets (Mangel et al. 2011, Pizarro 2008). Illegal fishing techniques (e.g. dynamite fishing) are a frequent problem in several localities of the Peruvian coast, such as Huarmey (Valqui 2012) and Paracas (Apaza et al. 2004, Valqui 2012). Industrial ships have frequently been observed fishing closer to the coast than allowed by law (Apaza et al. 2004), perturbing the coastal habitat on a broader scale. Another threat for Marine Otter is accidental death by entanglement (bycatch) in fishing nets (Brownell 1978, Mangel and Alfaro-Shigueto 2004, Pizarro 2008) and in crab pots (Medina-Vogel et al. 2004), although the dimension of these mortality cases is unknown.

Urban development within the region results in an increase in domestic and feral dogs, cats, and rats, which can introduce infectious diseases (Mangel et al. 2011). Around human settlements, large dens with terrestrial entrances may be occupied by dogs, cats and rats, displacing the Marine Otter from its reproduction, feeding and resting areas (Apaza et al. 2003, Valqui 2012). Dog attacks are increasingly reported in several locations of the distribution (Medina-Vogel et al. 2008, Mangel et al. 2010, Vianna et al. 2010).

Releases from mining tailings and sewage into the ocean expose Marine Otters to heavy metals, pesticides and other toxic elements. Heavy metals and other toxic substances can be diffused through currents and progressively transmitted through the food chain, at least at a regional level (Valqui 2004, Apaza et al. 2004). Oil spillage and extreme noise affect the species in areas near beach resorts in the vicinity of big cities (Valqui 2004) and in several centres of industrial fishing activity like Chimbote (probably the most important fishing port on the Peruvian coast) and mining cities Ite, Ilo and Marcona in Peru (Apaza et al. 2004). Oil spills in ports are a constant impact in central Chile, generating broad damage to the ecosystems that Marine Otters inhabit. Spills of domestic effluents reach the ocean directly or through rivers (Hinrichsen 1998, Thorne-Miller 1999) and affect the Marine Otter environments.

From central to northern Chile, the need for water for industrial use and human consumption has generated the search for solutions such as desalination plants. The impact generated by this is not well studied in the case of otters and is an added concern for populations in these areas.

Chile is one of the top ten countries in aquaculture production, and the deep and long-term impacts of the industry on rivers and marine ecosystem will expose the species to bacteria, viruses and antibiotics.

Recent development plans for infrastructure, such as dams in Arequipa, may impact Marine Otter presence in the known freshwater population far from the coast (Valqui et al. 2018a, Ugarte-Nuñez 2021).

Laws protect this endangered species in Peru and Chile, but enforcement is very weak. If an otter is killed or poached, the perpetrators may be identified, photographed or filmed, and still no legal action is taken. Rules in natural protected areas such as no hunting, fishing, poaching, or trespassing are not always respected.

Global natural factors like the El Niño Southern Oscillation (ENSO) also may considerably affect the Marine Otter population (Vianna et al. 2010), due to the more or less drastic climatic and oceanographic changes that cause mortality of several marine communities from fish to mammals (Apaza and Figari 1999, Wang and Fiedler 2006).

Habitats préférentiels (classification IUCN)

  • 10_1Marine Oceanic - Epipelagic (0-200m)
  • 12_1Marine Intertidal - Rocky Shoreline
  • 13_2Marine Coastal/supratidal - Coastal Caves/Karst
  • 13_5Marine Coastal/Supratidal - Coastal Freshwater Lakes
  • 9_2Marine Neritic - Subtidal Rock and Rocky Reefs
  • 13_1Marine Coastal/Supratidal - Sea Cliffs and Rocky Offshore Islands
  • 13_4Marine Coastal/Supratidal - Coastal Brackish/Saline Lagoons/Marine Lakes
  • 5_1Wetlands (inland) - Permanent Rivers/Streams/Creeks (includes waterfalls)
  • 5_5Wetlands (inland) - Permanent Freshwater Lakes (over 8ha)
  • 12_2Marine Intertidal - Sandy Shoreline and/or Beaches, Sand Bars, Spits, Etc
  • 12_5Marine Intertidal - Salt Marshes (Emergent Grasses)
  • 9_10Marine Neritic - Estuaries
Mesures de conservation recommandéesExpert
The Marine Otter is protected in Argentina, Chile, and Peru. It is listed in Appendix I of CITES and in Appendix I of the Bonn Convention (Convention on the Conservation of Migratory Species of Wild Animals (CMS)).

The Global Otter Conservation Strategy for the species (Valqui et al. 2018b) recommends priority actions that include:

An initiative to establish a regional conservation area in southern Peru -- Area de Conservación Regional Marino Costero Morro Sama, Tacna -- was started around 2003, but effective implementation stopped in 2006 because of a change in government, and the situation has not progressed since then. The area is the only otter hotspot on the Peruvian coast (with about 88 individuals in 55 km of coast) (Alfaro and Mangel 2008). Thus, the initiative of establishing a protected area containing an otter hot spot should be supported and completed. A strategy to protect otter habitats along the entire coast, coupled with initiatives to create specific regional conservation areas, is a challenging, but ideal goal for Marine Otter protection. Thirty-four existing natural protected areas in Peru and another ten in Chile could host artificial habitats, such as wave breakers, and specially designed artificial otter habitats. These should be visibly advertised to raise awareness of the Marine Otter’s presence to local communities. A reassessment is needed concerning the construction of two hydroelectric power stations, on the Colca-Majes River and the Cotahuasi-Ocoña River, both in Peru, and inhabited by the Marine Otter. Specific mitigation measures for impacts on wildlife should be considered. Dam construction should be approved only if careful and explicit mitigation measures are put in place. An effective programme to control invasive feral dogs, cats, and rats should be developed, and should be paired with studies on prevalence of transmittable diseases, especially in populations near human settlements. In Chile, studies on disease transmission to otters are already being conducted. Environmental education programmes should be carried out, such as the one by the NGO Chinchimén and Pro Delphinus, aimed at the general public and the young people who are the stakeholders of the future and will help to develop sustainable activities in their region. In order to stem further declines, studies should be undertaken to explain why the distribution of the Marine Otter is discontinuous along its coastal range. Moreover, both the northern limit and southern limits of its distribution need to be clarified through surveys (Alfaro et al. 2011). Although not all fishermen consider otters to be pests, some do, and may kill them “just in case.” Fishermen can be informed through awareness programmes that the amount of damage otters do has a minor economic impact. Reintroduction programmes are not recommended until more is known about the reasons for the decline of Marine Otter populations. High logistical and economic efforts are needed for such programmes, and efforts should concentrate on habitat protection and research for the time being.
Actions de conservation (12)Expert
  • 1_1Site/area protection
  • 1_2Resource & habitat protection
  • 2_1Site/area management
  • 2_3Habitat & natural process restoration
  • 3_2Species recovery
  • 4_1Formal education
  • 4_2Training
  • 4_3Awareness & communications
  • 5_1_3Sub-national level
  • 5_4_2National level
  • 5_4_3Sub-national level
  • 6_1Linked enterprises & livelihood alternatives
Stress écologiques (40)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_3Indirect ecosystem effects
  • 1_3Indirect ecosystem effects
  • 1_3Indirect ecosystem effects
  • 1_3Indirect ecosystem effects
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_3_7Reduced reproductive success
Usage & commerce (1)Expert
  • 10Wearing apparel, accessories
    subsistance
Priorités de recherche (7)Expert
  • 1_1Taxonomy
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_5Threats
  • 1_6Actions
  • 2_1Species Action/Recovery Plan
  • 3_1Population trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Neotropical

Systèmes (terrestre/eau douce/marin)

TerrestrialFreshwater (=Inland waters)Marine

Zones de pêche FAO

Atlantic - southwestPacific - southeast
Références bibliographiques (30)Expert
  1. IUCN. 2022. The IUCN Red List of Threatened Species. Version 2022-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 08 December 2022).
  2. Ugarte-Nuñez, J.A. 2021. Sea otter (Lontra felina) in the Andes of southern Peru. <i>Ciencia & Desarrollo</i> 20(1): 71-77.
  3. Valqui, J., Alfaro, J., Calvo, C. Verdi, R. 2018b. Marine otter. In: Duplaix, N. and M. Savage (eds), <i>Global Otter Conservation Strategy</i>, pp. 90-95. IUCN/SSC Otter Specialist Group, Salem, Oregon, USA.
  4. Valqui, J., Arce, A, Gonzales, F., Ruelas, C., Delgado, W., Zanabria, U., Zeballos, H., Santa-María, M., Medina-Vogel. G. 2018a. Nueva distribucion de la nutria marina Lontra felina en Arequipa, Peru. <i>SOLAMAC, Lima</i>.
  5. Pacifici, M., Santini, L., Di Marco, M., Baisero, D., Francucci, L., Grottolo Marasini, G., Visconti, P. and Rondinini, C. 2013. Generation length for mammals. <i>Nature Conservation</i> 5: 87–94.
  6. Valqui, J. 2012. The marine otter <i>Lontra felina</i> (Molina, 1782): A review of its present status and implications for future conservation . <i>Mammalian Biology </i> 77: 75-83.
  7. Alfaro-Shigueto, J., Valqui, J., and Mangel, J.C. 2011. Nuevo registro de la nutria marina <i>Lontra felina</i> (Molina, 1782) al norte de su distribución actual. <i>Ecología Aplicada </i> 10(2): 87-91.
  8. Alfaro-Shigueto, J., Mangel, J. C., Pajuelo, M., Dutton, P. H., Seminoff, J. A., & Godley, B. J. 2010. Where small can have a large impact: structure and characterization of small-scale fisheries in Peru. <i>Fisheries Research</i> 106(1): 8-17.
  9. Mangel J.C., Whitty, T., Medina-Vogel, G., Alfaro-Shigueto, J., Caceres, C. and Godley, B.J. 2010. Latitudinal variation in diet and patterns of human interaction in the marine otter. <i>Marine Mammal Science </i> 30: 95-96.
  10. Valqui, J., Hartl G.B., Zachos, F.E. 2010. Non-invasive genetic analysis reveals high levels of mtDNA variability in the endangered South-American marine otter (<i>Lontra felina</i>). <i>Conservation Genetics </i> 11: 2067-2072.
  11. Ulloa, R., Zambrano, M. and Chevarria, A., 2010. <i>Expediente Tecnico Area de conservación regional Morro Sama-Quebrada de Burros Tacna</i>. Perù.
  12. Vianna. J., Ayerdi, P., Medina-Vogel, G., Mangel, J.C., Zeballos, H., Apaza, M. and Faugeron, S. 2010. Phylogeography of the Marine Otter (<i>Lontra felina</i>): historical and contemporary factors determining its distribution. <i>Journal of Heredity </i> 101(6): 676-689.
  13. Ruiz, E. 2009. Estudio etológico de la nutria marina <i>Lontra felina</i> (Molina, 1782) en una ambiente antrópico, la bahía de Pucusana -Lima, Perú de junio a agosto del 2008. Tesis para optar el título de Biólogo, Universidad Nacional Agraria La Molina (UNALM). .
  14. Pizarro, J. 2008. Mortality of the marine otter (Lontra felina) in Southern Peru. <i>IUCN Otter Spec. Group Bull.</i> 25(2): 94-99.
  15. Cassini, M.H. 2008. Present status of <i>Lontra felina</i> in Argentina. <i>Endangered Species Update </i> 25(2): 57-60.
  16. Medina-Vogel, G., Merino, L.O., Monsalve Alarcón, R. and Vianna, J. de A. 2008. Coastal-marine discontinuities, critical patch size and isolation: implications for marine otter conservation. <i>Animal Conservation</i> 11: 57-64.
  17. Koepfli, K.-P., Deer, K.A., Slater, G.J., Begg, C., Begg, K., Grassman, L., Lucherini, M., Veron, G. and Wayne, R.K. 2008. Multigene phylogeny of the Mustelidae: resolving relationships, tempo and biogeographic history of a mammalian adaptive radiation. <i>BMC Biology</i> 6: 10. doi:10.1186/1741-7007-6-10.
  18. Medina-Vogel, G., Boher, F., Flores, G., Santibanez, A. and Soto-Azat, C. 2007. Spacing behavior of marine otters (<i>Lontra felina</i>) in relation to land refuges and fishery wastes in Central Chile. <i>Journal of Mammology</i> 88: 487–494.
  19. Medina-Vogel, G., Bartheld, J.V.L., Alavarez, R.E. and Delgado, C.R. 2006. Population assessment and habitat use by marine otter (<i>Lontra felina</i>) in Southern Chile. <i>Wildlife Biology</i> 12: 191–199.
  20. Sánchez, R. and Ayala, L. 2006. Evaluacion de la distribucion y abundancia del gato marino <i>Lontra felina</i> en la costa central y norte del Peru durante el otono del 2006. Reporte APECO.
  21. Wang, C. and Fiedler, P.C. 2006. ENSO variability and the eastern tropical Pacific: A review. <i>Progress in Oceanography</i> 69: 239-266.
  22. Mangel, J.C. and Alfaro-Shigueto, J. 2004. Comunidades pesqueras y la conservacion de la nutria marina (<i>Lontra felina</i>) en el sur de Peru. <i>Revista de Conservación Regional </i> 2: 5-10.
  23. Apaza, M., Valqui, J., Mangel, J., Roca, M., Alfaro, J., Santillan, L., Perret, J.P., Onton, G., Castaneda, C., Munemura, G., Tovar, A. 2004. Estado de Conservación de <i>Lontra felina</i> (Molina, 1782) en la Costa Peruana. Reporte para la Comisión Permanente del Pacífico Sur, Lima.
  24. Medina-Vogel, G., Delgado-Rodriguez, C., Alvarez, R.E. and Bartheld, J.L. 2004. Feeding ecology of the marine otter (<i>Lutra felina</i>) in a rocky seashore of the south of Chile. <i>Marine Mammal Science</i> 20(1): 134–144.
  25. Valqui, J. 2004. Comportamiento de la nutria marina <i>Lontra felina</i> (Molina, 1782) en una ambiente antrópico, la bahía de Pucusana -Lima, Perú. Tesis para optar el título de Biólogo, Universidad Nacional Agraria La Molina (UNALM). .
  26. Apaza, M., Valqui, J. and Castañeda, C. 2003. Estado de Conservación de las Poblaciones de <i>Spheniscus humboldti</i> y <i>Lontra felina</i> en la Costa Norte del Perú. Instituto Nacional de Recursos Naturales (INRENA), Lima.
  27. Majluf, P., Babock, E., Riveros J.C., Arias, M. and Alderete, W. 2002. Catch and Bycatch of Sea Birds and Marine Mammals in the Small-Scale Fishery of Punta San Juan, Peru. <i>Conservation Biology </i> 16(5): 1333-1343.
  28. Mattern, T., Ellenberg, U. and Luna-Jorquera, G. 2002. A South American Marine Otter Lontra felina preys upon chicks of the Peruvian Diving Petrel <i>Pelecanoides garnotii</i>. <i>Marine Ornithology </i> 30: 95-96.
  29. Moreno, C. 2001. Community patterns generated by human harvesting on Chilean shores: a review. <i>Aquatic Conservation </i> 11: 19-30.
  30. Sielfeld, W.K. and Castilla, J.C. 1999. Estado de conservación y conocimiento de las nutrias en Chile. <i>Estudios Oceanológicos</i> 18: 69-79.
Évaluateurs & contributeurs (2)Expert
assessor
Mangel, J., Alfaro-Shigueto, J., Verdi, R. & Rheingantz, M.L.
evaluator
Hussain, S.A. & Duplaix, N.

Mangel, J., Alfaro-Shigueto, J., Verdi, R. & Rheingantz, M.L. 2022. Lontra felina. The IUCN Red List of Threatened Species 2022: e.T12303A215395045. Accessed on 05 May 2026.

Traits biologiques

20 valeurs · 7 sources

Morphologie(4)

Masse adulte
11 kg
PanTHERIA
Longueur
67,7 cm
PanTHERIA
Masse naissance
-999000 mg
PanTHERIA
Masse au sevrage
-999000 mg
PanTHERIA

Cycle de vie(1)

Longévité max
-999 mois
PanTHERIA
Voir 15 traits de plus (2 catégories)

Reproduction(6)

Taille de portée
3
PanTHERIA
Sevrage
-999 j
PanTHERIA
Portées par an
-999
PanTHERIA
Gestation
2,5 mois
PanTHERIA
Intervalle naissances
1 ans
PanTHERIA
Maturité sexuelle
-999 j
PanTHERIA

Écologie & habitat(9)

Invertébrés (%)
70 %
elton_mammals
Graines (%)
0 %
elton_mammals
Fruits (%)
0 %
elton_mammals
Nectar (%)
0 %
elton_mammals
Charognard (%)
0 %
elton_mammals
Poissons (%)
30 %
elton_mammals
Autre végétal (%)
0 %
elton_mammals
Vert. ectothermes (%)
0 %
elton_mammals
Vert. endothermes (%)
0 %
elton_mammals

Sources priorisées par qualité scientifique (peer-reviewed spécialisées → Wikidata fallback). Unités auto-converties, valeur max retenue en cas de mesures multiples. Méthodologie · Citations.

Répartition mondiale

Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.

Consulter sur les bases externes

Observations & statuts

Cartographie

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (7)— redirigent vers cette page

  • Lutra brachydactylaWagner, 1841
  • Lutra californicaGray, 1837
  • Lutra felina(Molina, 1782)
  • Lutra montanaTschudi, 1844
  • Lutra peruviensisGervais, 1841
  • Mustela chilensisKerr, 1792
  • Mustela felinaMolina, 1782

Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).