Common Names: No Common Names
Synonyms: No Synonyms
| Red List Status | |
|---|---|
| EN - Endangered, B1ab(iii)+2ab(iii) (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)
Asparagus radiatus has a restricted distribution, with an estimated extent of occurrence of 40.543 km2 and an area of occupancy of 24 km2.
Although part of its range falls within a protected area, there are
ongoing threats to its habitat from timber harvesting. Based on this, it
has been assessed as Vulnerable, under Criteria B1 and B2.
Date last seen: 2020
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
This species is known from the Lubombo mountains in north eastern Eswatini, and the neighbouring Goba area in Mozambique.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 24 | The estimated area of occupancy has been based on 8 records for this species. 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 | There currently is no confirmed decline in the habitat for this species. |
| Extreme fluctuations in area of occupancy (AOO) | Justification |
|---|---|
| No | No extreme fluctuations in area of occupancy are known. |
| Estimated extent of occurrence (EOO)- in km2 | EOO estimate calculated from Minimum Convex Polygon | Justification |
|---|---|---|
| 40.543 | true | The estimated extent of occurrence has been based on 8 records for this species and was calculated using GeoCAT (Bachman et al. 2011). This is likely to be an overestimate, due to the habitat requirement of forested ravines; the extent of occurrence includes areas unsuited to this species. |
| Continuing decline in extent of occurrence (EOO) | Qualifier | Justification |
|---|---|---|
| No | Inferred | At this stage, there is no known decline in extent of occurrence for this species. |
| Extreme fluctuations in extent of occurrence (EOO) | Justification |
|---|---|
| No | No extreme fluctuations in extent of occurence are known at this point in time. |
| Number of Locations | Justification |
|---|---|
| 4 | Eight localities have been recorded for this species to date. Based on the distribution of these localities, it is estimated that this forms 4 locations. |
| Continuing decline in number of locations | Qualifier | Justification |
|---|---|---|
| No | Inferred | There is no known decline in number of locations for this species. |
| Extreme fluctuations in the number of locations | Justification |
|---|---|
| No | There is no known fluctuation in the number of locations for this species. |
| Very restricted in area of occupancy (AOO) and/or # of locations | Justification |
|---|---|
| No | This species has been recorded from 8 localities, and the estimated area of occupancy is 24 km2. This might be an over-estimation due to the specific habitat requirements for this species. |
Elevation Lower Limit (in metres above sea level): 95
Elevation Upper Limit (in metres above sea level): 455
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 |
| Mozambique | Extant | Native | - | Resident |
Large Marine Ecosystems: (Not specified)
FAO Marine Areas: (Not specified)
This species has been recorded from eight localites within the Lubombo Mountains in Eswatini and in the adjacent Goba area in Mozambique. It is uncommon at these localities. No detailed population surveys have been conducted.
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 species is found on dry rocky slopes on rhyolite, in Androstachys johnsonii dry forest. This area falls within the vegetation type Southern Lebombo Bushveld (SVI16) (Mucina et. al. 2018).
| Habitat | Season | Suitability | Major Importance? |
|---|---|---|---|
| 1.5. Forest -> Forest - Subtropical/Tropical Dry | - | Suitable | Yes |
| Continuing decline in area, extent and/or quality of habitat? | Qualifier | Justification |
|---|---|---|
| Yes | Inferred | There is ongoing pressure on the habitat for this species due to cutting of timber. |
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 survival of this species is dependent on the continued existence of its habitat, in Androstachys johnsonii forests in the Lubombo Mountains. Some of the existing forests may be at risk from timber harvesting.
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 |
|---|---|---|---|
| 5.3.1. Biological resource use -> Logging & wood harvesting -> Intentional use: (subsistence/small scale) [harvest] | Ongoing | Minority (<50%) | Slow, Significant Declines |
The range of the population of this species is included both in Mlawula Nature Reserve, and Shewula and Mhlumeni community conservation areas. The community conservation areas at this stage do not provide protection against timber harvesting which could result in habitat degradation.
| Action Recovery Plan | Note |
|---|---|
| No | - |
| Systematic monitoring scheme | Note |
|---|---|
| No | - |
| Conservation sites identified | Note |
|---|---|
| Yes, over part of range | The range of the population is included in Mlawula Nature Reserve, as well as Shewula and Mhlumeni community conservation areas. |
| Occur in at least one PA | Note |
|---|---|
| Yes | Recorded from Mlawula Nature Reserve, as well as Shewula and Mhlumeni community conservation areas. |
| Percentage of population protected by PAs (0-100) | Note |
|---|---|
| 51-60 | - |
| Area based regional management plan | Note |
|---|---|
| No | - |
Invasive species control or prevention: (Not specified)
| 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 | The protection of the Androstachys johnsonii forests would be essential for the long term survival of this species. |
| 3.4.2. Species management -> Ex-situ conservation -> Genome resource bank | No material has been collected yet for ex-situ conservation of this species. |
| Research | Note |
|---|---|
| 1.2. Research -> Population size, distribution & trends | More fieldwork is required to determine the extent of the population of this species as well as any population trends. |
| 1.3. Research -> Life history & ecology | There is a need for more information on the life history and ecology of this species for conservation planning purposes. |
| 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.