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: 2023-01-21
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)
Eragrostis comptonii has a very restricted distribution, with an estimated extent of occurrence of 387.032 km2 and an area of occupancy of 16 km2.
There are ongoing threats to its habitat from overgrazing by livestock,
and most of the known range does not fall within protected areas. Based
on this, it has been assessed as Endangered, under Criteria B1 and B2.
Date last seen: 1986
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
This species is known from four localities in north-western Eswatini.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 16 | This species is known from four localities. 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 |
|---|---|---|
| 387.032 | true | The extent of occurrence is based on the four localities recorded for this species, calculated using GeoCAT (Bachman et al. 2011). The older records do not include detailed locality information, so the coordinates have been estimated from the locality descriptions. |
| Continuing decline in extent of occurrence (EOO) | Qualifier | Justification |
|---|---|---|
| Unknown | - | There is no information with regard to any changes in extent of occurrence. |
| Extreme fluctuations in extent of occurrence (EOO) | Justification |
|---|---|
| Unknown | There is no known information with regard to fluctuations in extent of occurrence. |
| Number of Locations | Justification |
|---|---|
| 4 | Based on all available records, this species has been found in four localities. These are well separated, so are considered to form four locations. |
| Continuing decline in number of locations | Qualifier | Justification |
|---|---|---|
| Unknown | - | The localities have not been revisited recently, so there is no information with regard to possible decline in number of locations. |
| Extreme fluctuations in the number of locations | Justification |
|---|---|
| Unknown | There is no information with regard to extreme fluctuations in the number of locations. |
| Very restricted in area of occupancy (AOO) and/or # of locations | Justification |
|---|---|
| Yes | This plant is only known from four localities, giving an area of occupancy of 16 km2. |
Elevation Lower Limit (in metres above sea level): 830
Elevation Upper Limit (in metres above sea level): 1325
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)
This species is known from four localities in north-western Eswatini, but there is no information on population sizes or trends. It is possible that this is an under collected species, and occurs in additional localities in the area. None of the records are from recent years, but it has been assumed for the purposes of this assessment that the plant still occurs in these areas, as grasses have not been investigated recently in this part of the country.
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 description of this species includes the following with regard to habitat and ecology:
"Its
ecology is very poorly known. Judging from the notes on specimens it
tends to favour somewhat shady places such as at the foot of rocks or on
forest margins." (Winter, 1990). The localites where this plant
has been found all fall within the grassland biome, in KaNgwane Montane
Grassland (Gm16) (Mucina et. al. 2018).
| 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 |
|---|---|---|
| Yes | Inferred | There is extensive overgrazing in many parts of the grassland in the Eswatini highveld. |
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? Yes
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 ongoing threats to the highveld grassland in Eswatini, with extensive overgrazing in many areas. In addition there are land use changes, such as establishment of plantations or other forms of agriculture. It is currently not known if this would directly affect this plant.
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 |
|---|---|---|---|
| 2.3.2. Agriculture & aquaculture -> Livestock farming & ranching -> Small-holder grazing, ranching or farming | Ongoing | Majority (50-90%) | Slow, Significant Declines |
One of the four localities recorded for this species falls within Malolotja Nature Reserve.
| Action Recovery Plan | Note |
|---|---|
| No | - |
| Systematic monitoring scheme | Note |
|---|---|
| No | - |
| Conservation sites identified | Note |
|---|---|
| Yes, over part of range | This species has been recorded from within Malolotja Nature Reserve. |
| Occur in at least one PA | Note |
|---|---|
| Yes | This species has been recorded from within Malolotja Nature Reserve. |
| Percentage of population protected by PAs (0-100) | Note |
|---|---|
| 21-30 | There is no formal conservation for three of the four known localities for this species. |
| Area based regional management plan | Note |
|---|---|
| No | - |
| Invasive species control or prevention | Note |
|---|---|
| No | For most of the distribution of this species, there is no active invasive species control programme. |
| 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 of this species would enhance the probability of its survival. |
| Research | Note |
|---|---|
| 1.2. Research -> Population size, distribution & trends | There is currently no detailed information on population sizes or trends. In addition, more fieldwork is required to determine whether it occurs at more localities. |
| 1.3. Research -> Life history & ecology | More information is needed on the life history and ecology of this species for better planning of conservation measures to ensure its survival. |
| 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.
Winter, B.D. 1990. A new species of Eragrostis (Chlorideae) in the E. curvula alliance. Bothalia 20: 208.