Common Names: No Common Names
Synonyms: Ledebouria pusilla (U.Müll.-Doblies & D.Müll.-Doblies) J.C.Manning & Goldblatt
| Red List Status | |
|---|---|
| VU - Vulnerable, D2 (IUCN version 3.1) |
Is the reassessment subject to the 5-year rule? (Not specified)
Date of Assessment: 2023-01-26
Reviewed? (Not specified)
Assessor(s): Braun, K.
Reviewer(s): (Not specified)
Contributor(s): (Not specified)
Facilitators/Compilers: (Not specified)
Institution(s): (Not specified)
Acknowledgements: (Not specified)
Regions: Global
Regional Expert Questions: (Not specified)
Drimiopsis pusilla is known from only one small area, and
based on its very restricted area of occupancy and extent of occurrence,
has been assessed as Vulnerable under Criterion D2. Although the
localities are within a forestry area, it occurs in areas maintained as
firebreaks, and as it grows amongst rocks it has some protection from
livestock grazing, so it is inferred that there are no current threats
to this population.
Date last seen: 2023
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
Drimiopsis pusilla is known from a small area within the Eswatini highveld, within a forestry plantation.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 8 | This species is known from two localities within a small area. The estimated area of occupancy was calculated using GeoCAT (Bachman et al. 2011), with the standard 2x2 km grid cell being applied. |
| Continuing decline in area of occupancy (AOO) | Qualifier | Justification |
|---|---|---|
| No | Inferred | This species was still present in 2023, although the original locality was not revisited. |
| Extreme fluctuations in area of occupancy (AOO) | Justification |
|---|---|
| No | This species was found in the same locality in 1982 and again in 2000. It was found nearby in 2023. |
| Estimated extent of occurrence (EOO)- in km2 | EOO estimate calculated from Minimum Convex Polygon | Justification |
|---|---|---|
| 8 | true | This species is only known from one locality. The estimated extent of occurrence calculated using GeoCAT (Bachman et al. 2011) was 0 km2, less than the area of occupancy, so the higher figure has been used here. |
| Continuing decline in extent of occurrence (EOO) | Qualifier | Justification |
|---|---|---|
| No | Inferred | This species was still present in 2023, although the original locality was not revisited. |
| Extreme fluctuations in extent of occurrence (EOO) | Justification |
|---|---|
| No | This species was found in the same locality in 1982 and again in 2000. It was found nearby in 2023. |
| Number of Locations | Justification |
|---|---|
| 2 | This species has only been recorded from two localities about 1 km apart. Due to this separation they have been considered to be two separate locations. |
| Continuing decline in number of locations | Qualifier | Justification |
|---|---|---|
| Unknown | - | This species was found again in 2022, about 1 km from the previously recorded locality. More fieldwork is required to determine the full extent of this species' distribution. |
| Extreme fluctuations in the number of locations | Justification |
|---|---|
| Unknown | This species was found in the same locality in 1982 and again in 2000. Fieldwork in 2022 located it about 1 km away from the previously recorded locality. |
| Very restricted in area of occupancy (AOO) and/or # of locations | Justification |
|---|---|
| Yes | This species is only known from two localities within a small area. |
Elevation Lower Limit (in metres above sea level): 1390
Elevation Upper Limit (in metres above sea level): 1390
Depth Lower Limit (in metres below sea level): (Not specified)
Depth Upper Limit (in metres below sea level): (Not specified)
Depth Zone: (Not specified)
Map Status: (Not specified)
Biogeographic Realm: Afrotropical
| Country | Presence | Origin | Formerly Bred | Seasonality |
|---|---|---|---|---|
| Eswatini | Extant | Native | - | Resident |
Large Marine Ecosystems: (Not specified)
FAO Marine Areas: (Not specified)
This species was recorded from one locality in 1982, and again in 2000, but no details of population size were recorded. Although the area has not been revisited recently, it is presumed that the plant is still present in this locality, and that the population is stable. It was found again in 2023, in a nearby locality, with two small clusters of plants being observed.
Current Population Trend: (Not specified)
Number of mature individuals (=population size): (Not specified)
Extreme fluctuations? (in # of mature individuals): (Not specified)
Severely fragmented? (Not specified)
Continuing decline in mature individuals? (Not specified)
Continuing decline % in mature individuals within 1 generation or 3 years, whichever is longer (up to max. of 100 years in the future): (Not specified)
Continuing decline % in mature individuals within 2 generations or 5 years, whichever is longer (up to max. of 100 years in the future): (Not specified)
Continuing decline % in mature individuals within 3 generations or 10 years, whichever is longer (up to max. of 100 years in the future): (Not specified)
Extreme fluctuations in the number of subpopulations: (Not specified)
Continuing decline in number of subpopulations: (Not specified)
All individuals in one subpopulation: (Not specified)
Number of mature individuals in largest subpopulation: (Not specified)
Number of Subpopulations: (Not specified)
Percent Change in past: (Not specified)
Past Population Reduction Basis: (Not specified)
Causes of past reduction reversible? (Not specified)
Causes of past reduction understood? (Not specified)
Causes of past reduction ceased? (Not specified)
Percent Change in future: (Not specified)
Future Population Reduction Basis: (Not specified)
Both: Percent Change over any 10 year or 3 generation period, whichever is longer, and must include both past and future, future can't go beyond 100 years: (Not specified)
Both Population Reduction Basis: (Not specified)
Causes of both (past and future) reduction reversible? (Not specified)
Causes of both (past and future) reduction understood? (Not specified)
Causes of both (past and future) reduction ceased? (Not specified)
Probability of extinction in the wild within 3 generations or 10 years, whichever is longer, maximum 100 years: (Not specified)
Probability of extinction in the wild within 5 generations or 20 years, whichever is longer, maximum 100 years: (Not specified)
Probability of extinction in the wild within 100 years: (Not specified)
This species was found in rocky grassland, vegetation type KaNgwane Montane Grassland (Gm16), in the grassland biome (Mucina et. al. 2018).
| Habitat | Season | Suitability | Major Importance? |
|---|---|---|---|
| 4.7. Grassland -> Grassland - Subtropical/Tropical High Altitude | - | Suitable | - |
| Continuing decline in area, extent and/or quality of habitat? | Qualifier | Justification |
|---|---|---|
| Unknown | - | The locality where this plant was found falls within a forestry plantation, but on an unplanted area, maintained as a firebreak. Provided that this area is not planted up, the available habitat will not change. |
Generation Length: (Not specified)
Age at maturity: female or unspecified: (Not specified)
Age at Maturity: Male: (Not specified)
Size at Maturity (in cms): Female: (Not specified)
Size at Maturity (in cms): Male: (Not specified)
Longevity: (Not specified)
Average Reproductive Age: (Not specified)
Maximum Size (in cms): (Not specified)
Size at Birth (in cms): (Not specified)
Gestation Time: (Not specified)
Reproductive Periodicity: (Not specified)
Average Annual Fecundity or Litter Size: (Not specified)
Annual Rate of Population Increase: (Not specified)
Natural Mortality: (Not specified)
Does the species lay eggs? (Not specified)
Does the species give birth to live young: (Not specified)
Does the species exhibit parthenogenesis: (Not specified)
Does the species have a free-living larval stage? (Not specified)
Does the species require water for breeding? (Not specified)
Movement Patterns: (Not specified)
Congregatory: (Not specified)
System: Terrestrial
Wild relative of a crop? (Not specified)
Plant and Fungal Growth Forms: (Not specified)
Species not utilized: (Not specified)
No use/trade information for this species: true
General notes regarding trade and use of this species: (Not specified)
Local Livelihood: (Not specified)
National Commercial Value: (Not specified)
International Commercial Value: (Not specified)
End Use: (Not specified)
Is there harvest from captive/cultivated sources of this species? (Not specified)
Trend in level of total offtake from wild sources: (Not specified)
Trend in level of total offtake from domesticated sources: (Not specified)
Harvest Trend Comments: (Not specified)
Non-consumptive use of the species? (Not specified)
Explanation of non-consumptive use: (Not specified)
Livelihoods: (Not specified)
The localities where this plant was found fall within a forestry plantation, but on an unplanted area, maintained as a firebreak. Provided that this area is not planted up, the current land use provides some measure of protection. There is livestock grazing in the area, but as the plants grow amongst rocks, this would protect them from grazing.
No past, ongoing, or future threats exist to this species. (Not specified)
The threats to this species are unknown. true
Threats: (Not specified)
The localities where this plant was found fall within a forestry plantation, but on an unplanted area, maintained as a firebreak. Provided that the area is maintained as a firebreak area within the plantation and not planted up, this provides some measure of protection for this plant. Raising awareness with the plantation management of the presence of this species and the management actions to maintain it would assist with its conservation.
| Action Recovery Plan | Note |
|---|---|
| No | - |
| Systematic monitoring scheme | Note |
|---|---|
| No | - |
| Conservation sites identified | Note |
|---|---|
| No | - |
| Occur in at least one PA | Note |
|---|---|
| No | - |
| Percentage of population protected by PAs (0-100) | Note |
|---|---|
| 0 | - |
| Area based regional management plan | Note |
|---|---|
| No | - |
| Invasive species control or prevention | Note |
|---|---|
| No | - |
| Harvest management plan | Note |
|---|---|
| No | - |
| Successfully reintroduced or introduced benignly | Note |
|---|---|
| No | - |
| Subject to ex-situ conservation | Note |
|---|---|
| No | - |
| Subject to recent education and awareness programmes | Note |
|---|---|
| No | - |
| Included in international legislation | Note |
|---|---|
| No | - |
| Subject to any international management/trade controls | Note |
|---|---|
| No | - |
| Conservation Actions | Note |
|---|---|
| 3.4.2. Species management -> Ex-situ conservation -> Genome resource bank | Collection of material for ex-situ conservation of this species would reduce the risk of extinction for this species. |
| 4.3. Education & awareness -> Awareness & communications | If information on the existence of this species within the forestry plantation area is provided to plantation management, they would be in a better position to ensure the ongoing survival of this plant. |
| Research | Note |
|---|---|
| 1.2. Research -> Population size, distribution & trends | - |
| 1.3. Research -> Life history & ecology | - |
| Insufficient Information Available | All coded services should have an importance score of 5 - Not Known. |
|---|---|
| true | - |
Species provides no ecosystem services: (Not specified)
Ecosystem Services: (Not specified)
Bachman S, Moat J, Hill AW, de la Torre J and Scott B. 2011. Supporting Red List threat assessments with GeoCAT geospatial conservation tool. In: Smith V, Penev L (Eds) e-Infrastructure for data publishing in biodiversity science. . ZooKeys 150: 117-126.
Mucina, L., Rutherford, M.C. and Powrie, L.W. (Editors). 2018. The Vegetation Map of South Africa, Lesotho and Swaziland. South African National Biodiversity Institute. Available at: http://bgis.sanbi.org/Projects/Detail/186.