Common Names: No Common Names
Synonyms: No Synonyms
| Red List Status | |
|---|---|
| VU - Vulnerable, D2 (IUCN version 3.1) |
Is the reassessment subject to the 5-year rule? (Not specified)
Date of Assessment: 2023-01-25
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)
Syncolostemon comptonii has a very restricted distribution,
and is restricted to ultramafic soils. Its calculated estimated extent
of occurrence was smaller than the area of occupancy of 16 km2,
so the latter has been used for this assessment. Part of its
range falls within a protected area, but the remaining locations are at
risk from expansion of forestry plantations and ongoing livestock
grazing. Based on this, it has been assessed as Vulnerable, under
Criterion D2.
Date last seen: 1999
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
This species is known only from north west Eswatini, on ultramafic sites in Malolotja Nature Reserve and adjacent areas near the Nkomati River. The detailed locality information is from Donald McCallum's unpublished masters thesis.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 16 | The area of occupancy has been estimated from four recorded localities, 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 | The distribution of this species is partly included in Malolotja Nature Reserve, where it receives protection, and the remainder of the appropriate habitat has probably not declined in recent years, habitat loss due to forestry plantations having occurred at least 30 years ago. |
| Extreme fluctuations in area of occupancy (AOO) | Justification |
|---|---|
| No | No fluctuations in area of occupancy are known. |
| Estimated extent of occurrence (EOO)- in km2 | EOO estimate calculated from Minimum Convex Polygon | Justification |
|---|---|---|
| 16 | true | The estimated extent of occurrence is based on four localities, calculated using GeoCAT (Bachman et al. 2011). As this is smaller than the area of occupancy, the latter has been used for extent of occurrence. |
| Continuing decline in extent of occurrence (EOO) | Qualifier | Justification |
|---|---|---|
| No | Inferred | The distribution of this species is partly included in Malolotja Nature Reserve, where it receives protection, and the remainder of the appropriate habitat has probably not declined in recent years, habitat loss due to forestry plantations having occurred at least 30 years ago. |
| Extreme fluctuations in extent of occurrence (EOO) | Justification |
|---|---|
| No | There are no known extreme fluctuations in extent of occurrence for this species. |
| Number of Locations | Justification |
|---|---|
| 4 | Based on Donald McCallum's unpublished masters thesis, this species is known from four localities, and is limited to ultramafic soils. These localities may be subject to different threats and are considered to be for locations. |
| Continuing decline in number of locations | Qualifier | Justification |
|---|---|---|
| Unknown | - | There have been no recent surveys of this species, so its continued existence throughout its range is unknown. |
| Extreme fluctuations in the number of locations | Justification |
|---|---|
| No | There is currently no information on any extreme fluctuations in the number of locations for this species. |
| Very restricted in area of occupancy (AOO) and/or # of locations | Justification |
|---|---|
| Yes | The current known area of occupancy based on four records is 16 km2. This might be an overestimation due to this species being limited to ultramafic soils. |
Elevation Lower Limit (in metres above sea level): 690
Elevation Upper Limit (in metres above sea level): 940
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)
From Donald McCallum's unpublished masters thesis, this species is probably uncommon in the localities where it occurs, and is restricted to the serpentine sites. The fieldwork for this thesis was conducted in 1999, and there have been no more recent surveys of this species.
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)
There is very little information currently available on the habitats and ecology for this species, apart from its requirement for the geology being ultramafic areas. The vegetation types of the areas where it has been recorded are Swaziland Sour Bushveld (SV14) and Barberton Montane Grassland (Gm17) (Mucina et. al., 2018).
| Habitat | Season | Suitability | Major Importance? |
|---|---|---|---|
| 2.2. Savanna -> Savanna - Moist | - | Suitable | - |
| 4.7. Grassland -> Grassland - Subtropical/Tropical High Altitude | - | Suitable | - |
| Continuing decline in area, extent and/or quality of habitat? | Qualifier | Justification |
|---|---|---|
| Unknown | - | It is unknown at this stage whether there has been continuing decline of suitable habitat for this species, where its range falls outside Malolotja Nature Reserve. |
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 is potential habitat degradation occurring in the remaining appropriate habitats for this species which are found outside Malolotja Nature Reserve. This might be from expansion of forestry plantations as well as heavy grazing by livestock.
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 |
|---|---|---|---|
| 2.2.2. Agriculture & aquaculture -> Wood & pulp plantations -> Agro-industry plantations | Unknown | Minority (<50%) | Very Rapid Declines |
| 2.3.2. Agriculture & aquaculture -> Livestock farming & ranching -> Small-holder grazing, ranching or farming | Ongoing | Minority (<50%) | Unknown |
Part of the range for this species falls within Malolotja Nature Reserve, near the Nkomati River.
| Action Recovery Plan | Note |
|---|---|
| No | - |
| Systematic monitoring scheme | Note |
|---|---|
| No | - |
| Conservation sites identified | Note |
|---|---|
| Yes, over part of range | Part of the range for this species falls within Malolotja Nature Reserve, near the Nkomati River. |
| Occur in at least one PA | Note |
|---|---|
| Yes | This species has been found within Malolotja Nature Reserve. |
| Percentage of population protected by PAs (0-100) | Note |
|---|---|
| 41-50 | - |
| 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 | - |
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 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.
McCallum, D. Chapter 4. Conservation Status of Ultramafic Sites and Flora in Swaziland.
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.