PROVISIONAL COMPUTER-GENERATED RED LIST ASSESSMENTS OF MELIOLA
Meliola bouchardatiae
Assessment


Assessment   Distribution map   Evidence   Guide

Scientific name

Meliola bouchardatiae Hansf. [IndexFungorum. Index of Fungi 2: 193]

Synonyms

None noted.

Vernacular names

None known.

Taxonomic position

Meliolaceae, Meliolales, Sordariomycetes, Ascomycota, Fungi.

Red List assessment

Data Deficient [IUCN Red List Categories and Criteria: version 3.1. Level: global].

Rationale

This evaluation is based on 14 records [breakdown: Cybernome (1 record); IndexFungorum (1 record); other catalogues (1 record)]. There are 6 records with dates, the earliest 1828 (the species was first described in 1953), the most recent 1936. This species is recorded from 2 countries distributed through 2 continents and regions. This fungus is known to occur in association with 2 other species belonging in 3 genera.

This species is widely distributed and associated with more than one other genus, but there are no records more recent than 1960, and there are too few records to make any other evaluation.

Reasons for change from previous assessment

None: not previously assessed.

Date of assessment

29 November 2025.

Name/s of the assessor/s

D.W. Minter

Text documentation

Taxonomy. No comment.

Geographical distribution. Australia (New South Wales); Cuba.

IUCN area statistics [km²] AOO EOO
Pre-1961 12 8,917,900
1961-2000 0 0
Post-2000 0 0

Associated organisms and substrata [IUCN Red List status, if known]. Plantae (part): Amyris sp. (leaf); Bouchardatia neurococca Baill. (leaf).

Habitat and ecology.

Threats. Climate change. Not known. Habitat destruction. Not known. Persecution. Not known. Pollution. Not known.

Population. Not known. With no direct information, observation frequency over time, if available, can be considered as a proxy to infer current population trend; for species associated with trees, loss of woodland cover over time is another possible proxy. Observation frequency over time. The species was first described in 1953. There are 6 datable records of this species. The earliest is 1828 and the most recent is 1936. Loss of tree cover over time. This species occurs associated with trees in the following countries (percentage loss of tree cover between 2001 and 2024 in brackets): Australia (22%) [figures from 'Forest change' tab of Global Forest Watch]. Current trend (inferred). Long-term steep decline possibly driven by habitat destruction. The small number of datable records makes this inference very uncertain.

Conservation actions (in situ). None known.

Conservation actions (ex situ). Culture collections. Straininfo: check current status. Genome banks. European Nucleotide Archive: check current status; NCBI: check current status.

Economic impacts (positive). Bioremediation. None known. Biotechnology. None known. Cultural. None known. Ecosystem services. None known. Feed (animals). None known. Food (human). None known. Medical/veterinary. None known.

Economic impacts (negative). Biodeterioration. None known. Disease. None known. Invasiveness. None known.