Chimantá Poison Frog vs coast amaranth
Anomaloglossus rufulus compared with Amaranthus pumilus
Key Differences
- Chimantá Poison Frog is Near Threatened while coast amaranth is Extinct.
Taxonomic Classification
| Rank | Chimantá Poison Frog | coast amaranth |
|---|---|---|
| Kingdom | Animalia (Animals) | Plantae (Plants) |
| Phylum | Chordata (Chordates) | Magnoliophyta (Flowering Plants) |
| Class | Amphibia (Amphibians) | Magnoliopsida (Dicots) |
| Order | Anura (Frogs & Toads) | Caryophyllales (Caryophyllales) |
| Family | Aromobatidae | Amaranthaceae |
| Genus | Anomaloglossus | Amaranthus |
| Species | Anomaloglossus rufulus | Amaranthus pumilus |
Conservation Status
Chimantá Poison Frog
NT — Near Threatenedcoast amaranth
EX — ExtinctPhysical Characteristics
| Attribute | Chimantá Poison Frog | coast amaranth |
|---|---|---|
| Diet | — | — |
| Average Lifespan | — | — |
| Average Length | — | — |
| Average Weight | — | — |
Habitat & Geographic Range
Chimantá Poison Frog
Typically found in freshwater habitats, moist forests, and wetlands.
Found in Venezuela. Listed as Near Threatened, this species requires ongoing monitoring to prevent population decline.
coast amaranth
Typically found in diverse terrestrial habitats from tropical forests to temperate regions.
Found in Japan.
Chimantá Poison Frog
The Chimantá Poison Frog (Anomaloglossus rufulus) is a species in the genus Anomaloglossus. It is currently classified as Near Threatened on the IUCN Red List. Typically found in freshwater habitats, moist forests, and wetlands.
coast amaranth
Coast amaranth (Amaranthus pumilus) is an annual herb in the family Amaranthaceae, native to the Atlantic and Gulf coasts of the eastern United States, where it once grew on coastal foredunes, beach strand, and shell-hash substrates above the high tide line from New York south to South Carolina. It is a low-growing, fleshy plant with small, rounded leaves and inconspicuous green flowers typical of the genus. Coast amaranth is assessed as Extinct in the Wild by the IUCN, as it has not been reliably documented from wild populations since the mid-20th century; the last confirmed collections date to the 1960s. The species' decline and likely extinction resulted from intense human pressure on Atlantic coastal habitats through shoreline development, beach stabilisation, vehicular traffic on beaches, and increased storm frequency disrupting pioneer dune vegetation. It is federally listed as Threatened in the United States, though this listing predates confirmed extinction in the wild. A small number of ex-situ accessions may exist in botanical garden collections. Genetic material and seed banking efforts represent the only remaining conservation options for this critically reduced species.
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