Species Explorer

Browse and search species from the IUCN Red List and GBIF.

54,666 species

Ptilinopus arcanus

CR

Ptilinopus arcanus

Pop: Not assessed|Trend:

Aegotheles savesi

CR

Aegotheles savesi

Pop: Not assessed|Trend:

Loxioides bailleui

CR

Loxioides bailleui

Pop: Not assessed|Trend:

Ptilinopus huttoni

CR

Ptilinopus huttoni

Pop: Not assessed|Trend:

Zamia monticola

CR

Zamia monticola

Pop: Not assessed|Trend:

Ensete perrieri

CR

Ensete perrieri

Pop: Not assessed|Trend:

Fraxinus americana

CR

Fraxinus americana

Pop: Not assessed|Trend:

Heptapleurum curranii

CR

Heptapleurum curranii

Pop: Not assessed|Trend:

Cynanchum nielsenii

VU

Cynanchum nielsenii

Pop: Not assessed|Trend:

Horsfieldia obscurinervia

EN

Horsfieldia obscurinervia

Pop: Not assessed|Trend:

Myristica frugifera

VU

Myristica frugifera

Pop: Not assessed|Trend:

Myristica longepetiolata

EN

Myristica longepetiolata

Pop: Not assessed|Trend:

Heptapterus multiradiatus

CR

Heptapterus multiradiatus

Pop: Not assessed|Trend:

The threats to Bagrinho-do-tietê (Heptapterus multiradiatus) have not been formally assessed or documented by researchers. Without this threat assessment data, it's impossible to determine what specific dangers this fish species faces or how severe they might be. The status of threats to this species - whether they are increasing, stable, or decreasing - cannot be determined without proper scientific evaluation.

Myristica pilosigemma

CR

Myristica pilosigemma

Pop: Not assessed|Trend:

Kibatalia macgregorii

CR

Kibatalia macgregorii

Pop: Not assessed|Trend:

Ailurus fulgens

EN

Ailurus fulgens

Pop: ~1,000 in Nepal, ~10,000 globally|Trend:

The red panda faces multiple serious threats including the clearing of forests for logging and wood harvesting, expansion of livestock farming that destroys their habitat, and hunting by people who trap them for various purposes. Additional pressures come from road construction that fragments their living areas, invasive diseases, natural disasters like landslides, and climate-related changes that alter their mountain forest homes. All of these threats are currently ongoing and appear to be intensifying due to increasing human development in the regions where red pandas live.

Pseudoeurycea aquatica

CR

Pseudoeurycea aquatica

Pop: Not assessed|Trend:

The primary threats to the Aquatic Salamander have not been formally assessed or documented by conservation scientists. Without this threat assessment data, it's not possible to identify the specific dangers this species faces or understand what might be causing population changes. The status of threats to this species cannot be determined as increasing, stable, or decreasing due to the lack of available information.

Lecidea sarcogynoides

CR

Lecidea sarcogynoides

Pop: Not assessed|Trend:

Kibatalia puberula

EN

Kibatalia puberula

Pop: Not assessed|Trend:

Passiflora pamplonensis

CR

Passiflora pamplonensis

Pop: Not assessed|Trend:

Buellia asterella

CR

Buellia asterella

Pop: Not assessed|Trend:

Secamone racemosa

VU

Secamone racemosa

Pop: Not assessed|Trend:

Hopea quisumbingiana

EN

Hopea quisumbingiana

Pop: Not assessed|Trend:

Myristica laevis

EN

Myristica laevis

Pop: Not assessed|Trend:

Buellia violaceofusca

CR

Buellia violaceofusca

Pop: Not assessed|Trend:

Cercidospora macrospora

CR

Cercidospora macrospora

Pop: Not assessed|Trend:

Parinari pachyphylla

EN

Parinari pachyphylla

Pop: Not assessed|Trend:

Squatina squatina

CR

Squatina squatina

Pop: Not assessed|Trend:

Based on the provided threat data, the specific threats to the Angelshark (Squatina squatina) have not been assessed or documented in detail. Without a formal threat assessment, it's not possible to identify the particular dangers this species faces or describe how human activities or environmental changes may be affecting their populations. The current status of whether threats to this species are increasing, stable, or decreasing cannot be determined without proper threat evaluation data.

Heosemys depressa

CR

Heosemys depressa

Pop: Not assessed|Trend:

Based on the available information, the specific threats to the Arakan Forest Turtle have not been formally assessed or documented. Without a proper threat evaluation, it's unclear what particular dangers this species faces in the wild, such as habitat destruction, hunting, or other human activities. The status of whether threats are increasing, stable, or decreasing cannot be determined without this assessment data.

Myristica rubrinervis

VU

Myristica rubrinervis

Pop: Not assessed|Trend:

Lecidea diducens

CR

Lecidea diducens

Pop: Not assessed|Trend:

Dolichopetalum kwangsiense

VU

Dolichopetalum kwangsiense

Pop: Not assessed|Trend:

Gnetum arboreum

VU

Gnetum arboreum

Pop: Not assessed|Trend:

Actinodaphne bicolor

EN

Actinodaphne bicolor

Pop: Not assessed|Trend:

Bunolagus monticularis

CR

Bunolagus monticularis

Pop: Not assessed|Trend:

Alasmidonta raveneliana

CR

Alasmidonta raveneliana

Pop: Not assessed|Trend:

Based on the provided threat data, the primary threats to the Appalachian elktoe have not been formally assessed or documented. Without a proper threat evaluation, it's unclear what specific dangers this freshwater mussel species faces in its natural habitat. The status of whether threats are increasing, stable, or decreasing cannot be determined without this essential threat assessment data.

Carcharhinus borneensis

CR

Carcharhinus borneensis

Pop: Not assessed|Trend:

Actinodaphne dolichophylla

VU

Actinodaphne dolichophylla

Pop: Not assessed|Trend:

Actinodaphne samarensis

EN

Actinodaphne samarensis

Pop: Not assessed|Trend:

Hunga novoguineensis

EN

Hunga novoguineensis

Pop: Not assessed|Trend:

Cyrtidula hippocastani

CR

Cyrtidula hippocastani

Pop: Not assessed|Trend:

Dypsis ovobontsira

CR

Dypsis ovobontsira

Pop: Not assessed|Trend:

Marmosops handleyi

CR

Marmosops handleyi

Pop: Not assessed|Trend:

Ctenitis squamigera

CR

Ctenitis squamigera

Pop: Not assessed|Trend:

Adinandra leytensis

EN

Adinandra leytensis

Pop: Not assessed|Trend:

Adinandra macquilingensis

EN

Adinandra macquilingensis

Pop: Not assessed|Trend:

Alectryon fuscus

EN

Alectryon fuscus

Pop: Not assessed|Trend:

Cercidospora cladoniicola

CR

Cercidospora cladoniicola

Pop: Not assessed|Trend:

Eleutherodactylus karlschmidti

CR

Eleutherodactylus karlschmidti

Pop: Not assessed|Trend:

Hunga guillauminii

EN

Hunga guillauminii

Pop: Not assessed|Trend:

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