Chocolate Wattled Bat vs Clover midget

Chalinolobus morio compared with Phyllonorycter insignitella

Key Differences

• Chocolate Wattled Bat is Least Concern while Clover midget is Critically Endangered.

Taxonomic Classification

Rank	Chocolate Wattled Bat	Clover midget
Kingdom same	Animalia (Animals)	Animalia (Animals)
Phylum	Chordata (Chordates)	Arthropoda (Arthropods)
Class	Mammalia (Mammals)	Insecta (Insects)
Order	Chiroptera (Bats)	Lepidoptera (Butterflies & Moths)
Family	Vespertilionidae	Gracillariidae
Genus	Chalinolobus	Phyllonorycter
Species	Chalinolobus morio	Phyllonorycter insignitella

Evolutionary Relationship

Chocolate Wattled Bat and Clover midget share a common ancestor at the Kingdom level: Animalia. (Animals)

Conservation Status

Chocolate Wattled Bat

LC — Least Concern

Clover midget

CR — Critically Endangered

Physical Characteristics

Attribute	Chocolate Wattled Bat	Clover midget
Diet	—	—
Average Lifespan	—	—
Average Length	—	—
Average Weight	—	—

Habitat & Geographic Range

Chocolate Wattled Bat

Habitat

Typically found in diverse terrestrial and aquatic ecosystems.

Clover midget

Habitat

Found across multiple habitat types including temperate broadleaf and mixed forests, temperate coniferous forests, and boreal forests and taiga, among 8 distinct biome types within the Palearctic biogeographic realm. Populations are also found in montane and highland environments at higher elevations.

Range

Distributed across Belgium, Denmark, Norway, Russia, and Sweden. Currently classified as Critically Endangered on the IUCN Red List, this species faces significant conservation challenges across its range.

Chocolate Wattled Bat

The Chocolate Wattled Bat (Chalinolobus morio) is a small insectivorous bat in the family Vespertilionidae, endemic to Australia, where it is one of the more widespread members of the genus Chalinolobus — the wattled bats, named for the fleshy lobes (wattles) at the corners of the mouth. Chalinolobus morio is uniformly dark brown to chocolate-brown in colour, compact in build, and has the short, broad wings characteristic of bats that forage in cluttered forest environments at moderate to low altitudes. It is distributed across much of temperate and subtropical eastern Australia, southwestern Australia, and Tasmania, inhabiting diverse forest types from eucalypt woodland and mallee to tropical dry forest. The species roosts in tree hollows, bat boxes, and occasionally in buildings, sometimes forming small colonies. It feeds nocturnally on moths, beetles, mosquitoes, and other flying insects, using echolocation to detect and pursue prey. Like other hollow-dependent bats in Australia, populations are sensitive to the loss of large, old eucalypts with natural cavities. The IUCN classifies Chalinolobus morio as Least Concern given its broad distribution and relatively large population across Australia. Ongoing threats include hollow-bearing tree removal, roost disturbance, cat predation, and barbed wire entanglement.

Clover midget

The clover midget (Phyllonorycter insignitella) is a micro-moth in the family Gracillariidae, order Lepidoptera, known for its leaf-mining larval biology in which larvae feed within the tissue of leaves, creating distinctive blotch mines on their host plants. P. insignitella specializes on leguminous host plants including clovers (Trifolium species) and medicks (Medicago species), with larvae creating lower-surface blotch mines on leaflets. The mines are typically oval or irregular in shape, with the lower epidermis folded or puckered by larval feeding. Adults are small, narrow-winged moths typically one to two centimeters in wingspan, with the golden and white streaked forewing pattern characteristic of many gracillariids. The species is distributed in Europe, with confirmed records from Belgium, Denmark, Norway, Russia, and Sweden. It inhabits meadows, grasslands, clover fields, and other habitats where its leguminous host plants grow. P. insignitella is listed as Critically Endangered on the IUCN Red List, a status reflecting severe population decline across much of its former European range. The primary threats are agricultural intensification — including the loss of semi-natural grasslands, increased herbicide use eliminating host plant diversity, and the conversion of diverse legume-rich meadows to monoculture grasslands — which together have reduced both host plant availability and microhabitat connectivity required by this specialist species. Targeted grassland conservation efforts are essential for preventing extinction.