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: 2023-01-08
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)
Cineraria ngwenyensis has an extremely limited distribution,
its known population having declined drastically due to open cast iron
ore mining from 1964 to 1977. The surviving population has a
distribution with an estimated extent of occurrence of less than
its area of occupancy of 4 km2. Based on this it has been
assessed as Vulnerable under Criterion D2. There is a potential
threat from resumption of mining activities in the area which could
result in this species becoming Critically Endangered or even Extinct
within a short period of time if the mining activities cause loss of
habitat for this species.
Date last seen: 1995
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
This plant has only been found in the Ngwenya Mine area within Malolotja Nature Reserve, in Eswatini. There are records from five localities, but two of these were from an area which was removed during the operation of Ngwenya Mine, and therefore no longer exist.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 4 | This species is known from three remaining localities, the other two having been removed during the operation of Ngwenya Iron Ore Mine. 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): (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 |
|---|---|---|
| 4 | true | This species is known from three remaining localities, the other two having been removed during the operation of Ngwenya Iron Ore Mine. The estimated extent of occurrence calculated using GeoCAT (Bachman et al. 2011) was 0.111 km2, less than the area of occupancy, so the higher figure has been used here. |
Continuing decline in extent of occurrence (EOO): (Not specified)
Extreme fluctuations in extent of occurrence (EOO): (Not specified)
| Number of Locations | Justification |
|---|---|
| 3 | This species is known from three remaining localities, the other two having been removed during the operation of Ngwenya Iron Ore Mine. Further mining activities could affect any or all of these localities, so they have been considered to be 3 locations. |
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 known from three remaining localities, the other two having been removed during the operation of Ngwenya Iron Ore Mine. Further mining activities could affect any or all of these localities. |
Elevation Lower Limit (in metres above sea level): 1515
Elevation Upper Limit (in metres above sea level): 1680
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)
According to Cron et. al. (2006), this species is very rare and restricted in distribution with small populations, currently known from three localities.
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)
The species is found in the grassland biome,vegetation type KaNgwane Montane Grassland (Gm16) (Mucina et. al. 2018). According to Cron et. al. (2006), this species is found in the shade of rocks on mountain north-west facing spurs, near the summit of quartzite ridges.
| 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 | - | There is a possibility of further mining activities in the area, which could affect this species. However, if this species is restricted to the quartzite spurs, it might not be affected. |
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 a possibility of further mining activities in the area, which could affect this species. However, if this species is restricted to the quartzite spurs, it is possible that mining activities could be conducted without the destruction of the habitat for this species.
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 |
|---|---|---|---|
| 3.2. Energy production & mining -> Mining & quarrying | Past, Likely to Return | Whole (>90%) | Very Rapid Declines |
The entire distribution of this species falls within Malolotja Nature Reserve. However, in spite of this being a proclaimed protected area, it is possible that mining activities maybe resumed in the area, potentially affecting the remaining populations of this species. The plant is found on quartzite spurs, so it is possible that the mining activities might not directly be aimed at these areas, but there could be habitat loss due to mining infrastructure being established.
| Action Recovery Plan | Note |
|---|---|
| No | - |
| Systematic monitoring scheme | Note |
|---|---|
| No | - |
| Conservation sites identified | Note |
|---|---|
| Yes, over entire range | This species is only known from within Malolotja Nature Reserve. |
| Occur in at least one PA | Note |
|---|---|
| Yes | This species is only known from within Malolotja Nature Reserve. |
| Percentage of population protected by PAs (0-100) | Note |
|---|---|
| 91-100 | - |
| Area based regional management plan | Note |
|---|---|
| No | - |
| Invasive species control or prevention | Note |
|---|---|
| Unknown | There are some measures carried out within Malolotja to control invasive species, but it is not known whether these have included the area where this species is found. |
| 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 would enhance the probability of survival of this species. |
| Research | Note |
|---|---|
| 1.2. Research -> Population size, distribution & trends | More research is required into the population sizes and trends for this species, and more fieldwork to determine if this plant is found in any additional localities. |
| 1.3. Research -> Life history & ecology | Very little is currently known of the life history and ecology of this species. More information would assist with planning of any conservation measures for this plant. |
| 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.
Cron, G.V., Balkwill, K. & Knox, E.B. 2006. A revision of the genus Cineraria (Asteraceae, Senecioneae). Kew Bulletin 61: 449-535.