Common Names: No Common Names
Synonyms: No Synonyms
| Red List Status | |
|---|---|
| EN - Endangered, B1ab(iii,iv)+2ab(iii,iv) (IUCN version 3.1) |
Is the reassessment subject to the 5-year rule? (Not specified)
Date of Assessment: 2023-01-20
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)
Lobelia corniculata has a very restricted distribution, with an estimated extent of occurrence of 830.496 km2, with an area of occupancy of 20 km2.
Its habitat preference for moist areas along seasonal rivers and
drainage lines puts it at risk from alien plant encroachment by Chromolaena odorata and Lantana camara, these species being a major problem in the areas where Lobelia corniculata
has been found. This species is threatened not only by habitat
loss due to the alien plant species, but also by physical damage to the
habitat caused by alien plant control activities. In addition,
there is a threat of loss due to flooding of streams and rivers. Based
on this, it has been assessed as Endangered under Criteria B1 and B2.
Date last seen: 2022
Reason(s) for Change in Red List Category from the Previous Assessment: (Not specified)
Red List Index: (Not specified)
This species is known from north eastern Eswatini and from Hluhluwe in KwaZulu Natal, South Africa. The precise location information is not available for some of the older records, so it is likely that the upper elevation information included here is incorrect.
| Estimated area of occupancy (AOO) - in km2 | Justification |
|---|---|
| 20 | The estimated area of occupancy is based on six records which have locality information, calculated using GeoCAT (Bachman et al. 2011), with the standard 2x2 km grid cell being applied. One record has been excluded, based on habitat degradation at that locality. |
| Continuing decline in area of occupancy (AOO) | Qualifier | Justification |
|---|---|---|
| Unknown | - | Further fieldwork is required to determine whether there is any decline in area of occupancy. |
| Extreme fluctuations in area of occupancy (AOO) | Justification |
|---|---|
| Unknown | There is currently no information on any extreme fluctuations in area of occupancy. |
| Estimated extent of occurrence (EOO)- in km2 | EOO estimate calculated from Minimum Convex Polygon | Justification |
|---|---|---|
| 830.496 | true | The estimated extent of occurrence is based on seven records which have locality information, calculated using GeoCAT (Bachman et al. 2011). |
| Continuing decline in extent of occurrence (EOO) | Qualifier | Justification |
|---|---|---|
| Unknown | - | Further fieldwork is required to determine whether there is any decline in area of occupancy. |
| Extreme fluctuations in extent of occurrence (EOO) | Justification |
|---|---|
| Unknown | There is currently no information on any extreme fluctuations in extent of occurrence. |
| Number of Locations | Justification |
|---|---|
| 5 | The number of locations is a rough estimate based on locality descriptions on older herbarium specimens. |
| Continuing decline in number of locations | Qualifier | Justification |
|---|---|---|
| Yes | Inferred | Further fieldwork is required to determine whether there is any decline in number of locations, but this species might have been affected by spread of invasive species within Mlawula Nature Reserve, followed by the control measures to remove the alien species (Chromolaena and Lantana). |
| Extreme fluctuations in the number of locations | Justification |
|---|---|
| Unknown | There is no information on extreme fluctuations in number of locations for this species. |
| Very restricted in area of occupancy (AOO) and/or # of locations | Justification |
|---|---|
| Yes | Based on currently available information, this species has an area of occupancy of 20 km2. Its habitat requirement for moist areas means that this area of occupancy might be an over-estimate. |
Elevation Lower Limit (in metres above sea level): 155
Elevation Upper Limit (in metres above sea level): 640
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 |
| South Africa -> KwaZulu-Natal | Extant | Native | - | Resident |
Large Marine Ecosystems: (Not specified)
FAO Marine Areas: (Not specified)
This species is known from the north east of Eswatini and from one record in Hluhluwe Game Reserve in South Africa. No detailed population surveys have been conducted. The presence in South Africa requires confirmation, having last been recorded in 1955. Its continued presence in Eswatini has been confirmed by a record from 2022, but more fieldwork is required for the Eswatini localities, as some of the localities are in an area where there might have been habitat degradation due to alien invasive plants followed by clearing activities to remove these plants.
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 has been recorded from moist places, along seasonal rivers and drainage lines in grassveld and bushveld, vegetation types Tshokwane-Hlane Basalt Lowveld (SVI5), Zululand Lowveld (SVI23) and possibly Southern Lebombo Bushveld (SVI16) (Mucina et. al. 2018). The locality information for some of the older records is not accurate, so the records from Southern Lebombo Bushveld might well be from more lower lying areas nearby.
| Habitat | Season | Suitability | Major Importance? |
|---|---|---|---|
| 2.2. Savanna -> Savanna - Moist | - | Suitable | Yes |
| 5.2. Wetlands (inland) -> Wetlands (inland) - Seasonal/Intermittent/Irregular Rivers/Streams/Creeks | - | Suitable | Yes |
| Continuing decline in area, extent and/or quality of habitat? | Qualifier | Justification |
|---|---|---|
| Yes | Inferred | There has been an ongoing problem with regard to alien plant species spreading along the drainage lines, particularly within the Siphiso Valley in Mlawula 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)
In at least part of the range of this species, the requirement for moist habitat within savanna/woodland has meant that there has been habitat degradation due to invasive alien plant species (Chromolaena and Lantana). In Mlawula Nature Reserve, activities have been carried out to clear affected drainage lines, but it is not yet known whether this species still occurs in areas which were affected. In spite of control measures, it is likely that the invasive species will continue to affect the area. In addition to this, it is at risk from flooding of streams and rivers.
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 |
|---|---|---|---|
| 8.1.2. Invasive and other problematic species, genes & diseases -> Invasive non-native/alien species/diseases -> Named species | Ongoing | Unknown | Slow, Significant Declines |
| 8.1.2. Invasive and other problematic species, genes & diseases -> Invasive non-native/alien species/diseases -> Named species | Ongoing | Unknown | Slow, Significant Declines |
| 11.4. Climate change & severe weather -> Storms & flooding | Past, Likely to Return | Majority (50-90%) | Very Rapid Declines |
This species has been recorded from within Mlawula Nature Reserve and Mbuluzi Game Reserve in Eswatini, and from Hluhluwe Game Reserve in KwaZulu Natal. The Hluhluwe record requires confirmation as it was last recorded in 1955.
| 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 Mlawula Nature Reserve, Mbuluzi Game Reserve and Hluhluwe Game Reserve. |
| Occur in at least one PA | Note |
|---|---|
| Yes | This species has been recorded from within Mlawula Nature Reserve, Mbuluzi Game Reserve and Hluhluwe Game Reserve. |
| Percentage of population protected by PAs (0-100) | Note |
|---|---|
| 61-70 | There are two records from the Siteki area in Eswatini without precise locality information, but are presumed to be from nearby, not falling within a protected area. |
| Area based regional management plan | Note |
|---|---|
| No | - |
| Invasive species control or prevention | Note |
|---|---|
| Yes | There have been intensive alien plant control activities conducted in Mlawula Nature Reserve in an attempt to control the Chromolaena and Lantana spreading along drainage lines within the reserve. |
| 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 |
|---|---|
| 2.2. Land/water management -> Invasive/problematic species control | Ongoing invasive plant control measures are required to prevent habitat degradation for this species. |
| 3.4.2. Species management -> Ex-situ conservation -> Genome resource bank | No material has yet been collected 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 occurrence of this species and population trends. |
| 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.