Common Names: No Common Names
Synonyms: No Synonyms
| Red List Status | |
|---|---|
| LC - Least Concern, (IUCN version 3.1) |
Is the reassessment subject to the 5-year rule? (Not specified)
Date of Assessment: 2023-01-19
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)
Rhoicissus napaeus is an evergreen tendril climber, found
only within Eswatini. It is however quite widespread within the
country, with an estimated extent of occurrence of 3915.684 km2.
It appears to be tolerant of habitat degradation, and is therefore not
considered to be threatened. Based on this, it has been assessed
as Least Concern.
Date last seen: 2017
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
This species is found in the Eswatini middleveld, ranging from Mahamba in the south, to the Nyonyane area in the north.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 176 | The estimated area of occupancy for this species is based on 50 records, 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 appears to be tolerant of degraded habitats. |
Extreme fluctuations in area of occupancy (AOO): (Not specified)
| Estimated extent of occurrence (EOO)- in km2 | EOO estimate calculated from Minimum Convex Polygon | Justification |
|---|---|---|
| 3915.684 | true | The estimated extent of occurrence is based on 50 records, calculated using GeoCAT (Bachman et al. 2011). |
| Continuing decline in extent of occurrence (EOO) | Qualifier | Justification |
|---|---|---|
| No | Inferred | This species appears to be tolerant of degraded habitats. |
Extreme fluctuations in extent of occurrence (EOO): (Not specified)
| Number of Locations | Justification |
|---|---|
| 48 | The number of locations is based on 50 records for this species. |
| Continuing decline in number of locations | Qualifier | Justification |
|---|---|---|
| No | Inferred | This species appears to be tolerant of degraded habitats. |
Extreme fluctuations in the number of locations: (Not specified)
| Very restricted in area of occupancy (AOO) and/or # of locations | Justification |
|---|---|
| No | This species has been recorded from over 40 locations, with an estimated area of occupancy of 176 km2. |
Elevation Lower Limit (in metres above sea level): 425
Elevation Upper Limit (in metres above sea level): 1050
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)
In addition to herbarium specimens, photographic records and vegetation survey data, this species was included in the Swaziland Tree Atlas (Loffler, 2005), with a total of 50 records currently known for this plant.
Current Population Trend: Stable
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 is known from mainly savanna vegetation types, but also extends into the highveld grassland areas, namely Swaziland Sour Bushveld (SVI14), Granite Lowveld (SVI3), Ithala Quartzite Sourveld (Gs2) and KaNgwane Montane Grassland (Gm16) (Mucina et. al. 2018).
| Habitat | Season | Suitability | Major Importance? |
|---|---|---|---|
| 2.2. Savanna -> Savanna - Moist | - | Suitable | Yes |
| 4.7. Grassland -> Grassland - Subtropical/Tropical High Altitude | - | Suitable | No |
| Continuing decline in area, extent and/or quality of habitat? | Qualifier | Justification |
|---|---|---|
| No | Inferred | This species appears to survive in degraded habitats. |
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)
There are currently no known threats for this species.
No past, ongoing, or future threats exist to this species. (Not specified)
The threats to this species are unknown. (Not specified)
Threats: (Not specified)
Most of the range of this species falls outside formal protected areas, although it has been recorded from the Mlilwane North area.
| Action Recovery Plan | Note |
|---|---|
| No | - |
| Systematic monitoring scheme | Note |
|---|---|
| No | - |
| Conservation sites identified | Note |
|---|---|
| No | - |
| Occur in at least one PA | Note |
|---|---|
| Yes | This species has been recorded from within Mlilwane Game Sanctuary, in the Mlilwane North area. |
| Percentage of population protected by PAs (0-100) | Note |
|---|---|
| 1-10 | - |
| 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 | - |
Important Conservation Actions Needed: (Not specified)
Research Needed: (Not specified)
| 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, 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.
Loffler L., Loffler P. 2005. Swaziland Tree Atlas. Sabonet.
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.