Critical Biodiversity Areas for Limpopo (LCPv2_CBA_Layer.shp)
Critical Biodiversity Areas are the portfolio of sites that are required to meet the
region's biodiversity targets and need to be maintained in the appropriate condition for their category. A map of CBAs for Limpopo was produced as part of this plan and
sites were assigned to CBA categories based on their biodiversity characteristics, spatial configuration and requirement for meeting targets for both biodiversity pattern and ecological processes.
Simple
- Date (Publication)
- 2018-08
- Edition
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1.0
- Purpose
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Critical Biodiversity Areas are the portfolio of sites that are required to meet the region's biodiversity targets, and need to be maintained in the appropriate condition for their category. A map of CBAs for Limpopo was produced to guide development planning and inform decision makers with regard to biodiversity pattern and process.
- Status
- On going
- Maintenance and update frequency
- As needed
- Theme
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Critical Biodiversity Areas
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- Place
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South Africa
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Limpopo
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- Access constraints
- Copyright
- Use constraints
- otherRestictions
- Other constraints
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- Spatial representation type
- Vector
- Denominator
- 50000
- Language
- English
- Character set
- UTF8
- Topic category
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- Environment
- Begin date
- 2016-01-01
))
- Reference system identifier
- WGS 1984
Distributor
- OnLine resource
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A list of services published are available at this URL.
(
WWW:LINK-1.0-http--link
)
BGIS Map Services
- OnLine resource
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A list of spatial data-sets are available at this URL.
(
WWW:LINK-1.0-http--related
)
BGIS Spatial Datasets
- Hierarchy level
- Dataset
- Statement
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This section provides a technical description of the conservation features
and systematic planning process that underlies the revision of the Limpopo Conservation Plan. It is not designed to be a description of the conservation features; an explanation of their importance; or an explanation of systematic spatial biodiversity planning.
Bioregional plan requirements of a systematic conservation plan According to the "Guideline regarding the Determination of Bioregions and the Preparation and Publication of Bioregional Plans" (DEAT 2009) a bioregional plan needs to be a spatial plan showing terrestrial and aquatic features in the landscape that are critical for conserving biodiversity and maintaining ecosystem functioning. A bioregional plan must be based on a systematic biodiversity plan, which is a rigorous, data-driven approach for assessing the location, status and importance of a range of biodiversity features. In addition to the general requirement for a systematic conservation plan, the guidelines specify a range of key characteristics that a conservation plan would need to have before it can be considered to be systematic, and further, details a range of specific issues that need to be addressed in the systematic conservation plan.
This section of the document is aimed at clearly establishing that the underlying process undertaken for the Limpopo Conservation Plan v2 was both systematic in general, and was undertaken in a way which satisfies the requirements outlined in the "Guideline regarding the Determination of Bioregions and the Preparation and Publication of Bioregional Plans" (DEAT 2009).
Is the Limpopo Conservation Plan v2 a systematic conservation plan and does it
meet the guideline requirements?
The "Guideline regarding the Determination of Bioregions and the Preparation and Publication of Bioregional Plans" (DEAT 2009) identifies the key characteristics of a systematic conservation plan as being representation, persistence, quantitative targets, and efficiency and conflict avoidance. The approach taken in the Limpopo Conservation Plan v2 is evaluated below in terms these key characteristics:
- The principle of representation - the plan needs to identify the areas needed to
conserve a representative sample of all biodiversity patterns. Limpopo
Conservation Plan v2 utilizes a revised and updated version of the vegetation
types described in Mucina and Rutherford 2006. Data of the distribution of wetland and river systems was included. In addition to the broad habitats
described above, detailed data on the distribution and habitat requirements of a
range of threatened species were included. These species went through a robust
filtering process to ensure that only appropriate species were included, and that
the data quality was sufficient. Quantitative targets were set for all biodiversity
features to assess the degree to which the identified CBA network sufficiently
included all targets for biodiversity features was evaluated and reported on.
- The principle of persistence - the plan needs to identify the areas required to
support ecological and evolutionary processes that allow biodiversity to persist in
the long term. Limpopo Conservation Plan v2 focuses on three key areas to
ensure that biodiversity persists into the future.
o Climate change: The plan identifies a comprehensive terrestrial and
riverine corridors to ensure linkages are retained between key biodiversity
features; areas supporting climate change resilience (e.g. refuge habitats
and areas with diverse bioclimatic variables) were identified and included
as features in the plan; and other features such as ridges which include
important environmental gradients and linkages were included in the plan.
o Hydrological processes: Key wetland and river systems are include in the
plan. In addition, targets were set for identified priority freshwater
catchments and dolomite systems.
o Species requirements: Area requirements for each of the threatened
species include in the plan were identified and incorporated into the plan.
- Biodiversity targets - quantitative targets are set for both biodiversity pattern
and process features indicating how much of each feature is required to ensure
representation and persistence. Targets were set for all features included within
the plan. Targets ranged from 19% to 31% of original area for particular
vegetation types (with most targets being in the range 19-24%), up to 100% of
known habitat for key threatened species. The target setting process is aligned
with the processes used in other South African systematic plans.
- Efficiency and conflict avoidance - the configuration of priority areas must be
spatially efficient and where possible to avoid conflict with other land uses.
Limpopo Conservation Plan v2 utilizes a cost surface approach in MARXAN (Ball
et al., 2009) for selecting sites which were most important for meeting biodiversity targets for a range of features (this ensures spatial efficiency by
selecting sites which meet targets for a range of features first, and then selecting
the sites which are required for specific features only), while at the same time
avoiding areas with high levels of conflict with other land uses. Conflict with other
land uses was avoided both by being as efficient as possible in selecting sites,
where possible avoiding sites with existing incompatible land uses, aligning with
areas with compatible land uses and existing conservation initiatives (e.g.
biospheres and transfrontier conservation areas), and as far as possible avoiding
areas in close proximity to non-natural areas, roads and areas with mining rights
or known mineral deposits.
Therefore, it is clear that Limpopo Conservation Plan v2 meets all the requirements for being a systematic conservation plan. In addition to these general requirements, the guideline also specifies that a systematic conservation plan must be undertaken at an appropriate scale for informing land-use planning and decision-making, include both terrestrial and aquatic features, identify a portfolio of critical biodiversity areas required to meet targets, use up to date spatial data, use appropriate methods and technology, and be accompanied by a technical report. The Limpopo Conservation Plan v2 meets all of these requirements, viz.:
- Scale: This conservation plan is designed to be used at a scale of approximately 1:50 000, which is appropriate for informing land-use planning and decisionmaking. Although it can be used at a finer scale, this requires specialist
interpretation of the specific features identified in the systematic biodiversity plan.
As with all conservation plans, site visits by biodiversity specialists are necessary
for confirming the accuracy of data, and identifying the specific location and
condition of the biodiversity features when decisions are made at a site level.
- Terrestrial and aquatic features: Both terrestrial and aquatic features are included. Although there is less detail on aquatic habitat types than is included
for terrestrial habitats, variation within aquatic types is addressed by the inclusion
of a range of river and wetland associated species. Priorities for both rivers and
wetlands from the NFEPA project (Nel et al., 2011) were included.
- Identify a portfolio of critical biodiversity areas required to meet targets:
The set of Critical Biodiversity Areas described in the following section meet the
biodiversity targets for all features. Ecological corridors and other areas important for ensuring long term persistence were included in the network of Critical Biodiversity Areas and Ecological Support Areas.
- Use up to date spatial data: Limpopo Conservation Plan v2 makes use of the
most up-to-date, accurate, fine-scale GIS data available. In particular, the landcover data was significantly improved and updated.
- Use appropriate, scientifically sound, up-to-date methodology and techniques, including software and analyses: Limpopo Conservation Plan v2 uses standard and accepted systematic conservation planning methodology and techniques aligned with those used in other systematic conservation planning initiatives.
Available documentation: Limpopo Conservation Plan version 2: Technical Report FINAL.pdf
- File identifier
- edd6eb2a-28da-433c-ae5c-306350d1609f XML
- Metadata language
- English
- Character set
- UTF8
- Date stamp
- 2018-05-09T14:17:57
- Metadata standard name
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SANS 1878
- Metadata standard version
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FGDC-STD-001-1998
Overviews
Spatial extent
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