Common Names: No Common Names
Synonyms: No Synonyms
| Red List Status | |
|---|---|
| CR - Critically Endangered, B1ab(iii)+2ab(iii) (IUCN version 3.1) | |
| Possibly Extinct: | Yes |
| Possibly Extinct in the Wild: | No |
| Date Last Recorded (in the wild): | 1982 |
Is the reassessment subject to the 5-year rule? (Not specified)
Date of Assessment: 2023-01-10
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)
Hesperantha umbricola is only known from one specimen
collected in 1982, and the locality has since been transformed by
highway construction. It is however possible that the plant might
still occur at other localities nearby, as there are remaining areas
with a similar habitat. Because of this, the species has been
assessed as Critically Endangered under Criteria B1 and B2, with an
ongoing threat of urban development to its habitat.
Date last seen: 1982
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
This species is only known from one collection in 1982 from Mbabane in Eswatini. The locality has since been transformed by highway construction. It is however possible that the plant might still occur at other localities in the area.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 0 | This species is only known from one locality which has been transformed by highway construction. |
Continuing decline in area of occupancy (AOO): (Not specified)
Extreme fluctuations in area of occupancy (AOO): (Not specified)
| Estimated extent of occurrence (EOO)- in km2 | EOO estimate calculated from Minimum Convex Polygon | Justification |
|---|---|---|
| 0 | true | This species is only known from one locality which has been transformed by highway construction. The estimated extent of occurrence was calculated using GeoCAT (Bachman et al. 2011). |
Continuing decline in extent of occurrence (EOO): (Not specified)
Extreme fluctuations in extent of occurrence (EOO): (Not specified)
| Number of Locations | Justification |
|---|---|
| 0 | This species is only known from one locality which has been transformed by highway construction. It is possible that it might still occur in other localities in the vicinity. |
Continuing decline in number of locations: (Not specified)
Extreme fluctuations in the number of locations: (Not specified)
| Very restricted in area of occupancy (AOO) and/or # of locations | Justification |
|---|---|
| Yes | This species is only known from one locality which has been transformed by highway construction. |
Elevation Lower Limit (in metres above sea level): 1170
Elevation Upper Limit (in metres above sea level): 1170
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 | Possibly Extant | Native | - | Resident |
Large Marine Ecosystems: (Not specified)
FAO Marine Areas: (Not specified)
This species is only known from one locality which has been transformed by highway construction. There is the possibility that it might occur in locations with similar habitats in the vicinity.
Current Population Trend: Unknown
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 plant was collected in deep shade under a large boulder, growing with Dietes and Streptocarpus, on a rocky hillside above the centre of Mbabane. The plant was found in the grassland biome, in vegetation type KaNgwane Montane Grassland (Gm16) (Mucina et. al. 2018).
| Habitat | Season | Suitability | Major Importance? |
|---|---|---|---|
| 4.7. Grassland -> Grassland - Subtropical/Tropical High Altitude | - | Suitable | Yes |
| Continuing decline in area, extent and/or quality of habitat? | Qualifier | Justification |
|---|---|---|
| Yes | Inferred | This plant has only been found in one locality within the Mbabane urban area. Ongoing urban development provides a threat to the habitat. |
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)
This species is only known from one locality within the urban area, which was transformed by highway construction. Similar localities of this habitat do occur in the area, but are at risk from further urban development. As the micro-habitat for this species involves large granite boulders, it is possible that pockets of this habitat type might remain in spite of the urban development.
No past, ongoing, or future threats exist to this species. (Not specified)
The threats to this species are unknown. (Not specified)
| Threat | Timing | Scope | Severity |
|---|---|---|---|
| 1.1. Residential & commercial development -> Housing & urban areas | Ongoing | Minority (<50%) | Rapid Declines |
In spite of the loss of habitat from the one known locality for this species, it is possible that it still occurs within the general area. There is currently no formal conservation for this habitat in the Mbabane area, but establishment of small flora reserves within the Mbabane urban area could potentially protect the habitat for this species.
| 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 |
|---|---|
| 1.2. Land/water protection -> Resource & habitat protection | There is currently no formal conservation for this habitat in the Mbabane area, but establishment of small flora reserves within the Mbabane urban area could potentially protect the habitat for this species. |
| 3.4.2. Species management -> Ex-situ conservation -> Genome resource bank | If this plant can be found again, collection of material for ex-situ conservation would provide a means of preventing the extinction of this species. |
| Research | Note |
|---|---|
| 1.2. Research -> Population size, distribution & trends | Fieldwork is required in order to determine whether any plants of this species still exist in the wild. |
| 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.