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Koala Habitat Restoration Areas v1.0
Koala Habitat Restoration Area
2020-01-20T00:00:00
Version 1.0
20200120
Manager, Koala Policy and Oversight
Department of Environment and Science
Manager, Koala Policy and Oversight
GPO Box 2454,
Brisbane
Queensland
4001
SEQKoalaStrategy@des.qld.gov.au
AU
Manager, Koala Policy and Oversight
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Phascolarctos cinereus (koala) preferred areas for habitat restoration.
<DIV STYLE="text-align:Left;"><DIV><DIV><P><SPAN><SPAN>The </SPAN></SPAN><SPAN STYLE="font-style:italic;">Phascolarctos cinereus</SPAN><SPAN /><SPAN><SPAN>Koala Habitat Restoration Area (KHRA) provides the delineation of cleared areas under the Habitat Suitability Model (HSM) matrix rulesets 351, 350, 341 and 340 and applied to a Marxan restoration scenario. HSM rulesets are designated using rules defined by experts and through a modelling process. Further refinement of the KHRA removed areas where restoration was unsuitable in certain zones or areas. Restoration mapping for koala habitat is indicative and may be used to inform planning decisions, offsets policy and program delivery decisions</SPAN></SPAN></P></DIV></DIV></DIV>
© State of Queensland (Department of Environment and Science), 2020.
Queensland
Phascolarctos cinereus
Koala
Threatened species habitat
Habitat modelling
FAUNA Native
ECOLOGY Habitat
ECOLOGY Models
<DIV STYLE="text-align:Left;"><DIV><DIV><DIV STYLE="font-size:12pt"><P STYLE="margin:0 0 0 0;"><SPAN STYLE="font-size:10pt">PUBLIC Access - This material is licensed under a Creative Commons - Attribution 4.0 International license. The Department of Environment and Science requests attribution in the following manner: ©State of Queensland (Department of Environment and Science), </SPAN><SPAN STYLE="font-size:10pt">2020</SPAN><SPAN STYLE="font-size:10pt">.</SPAN></P><P><SPAN /></P></DIV></DIV></DIV></DIV>
The Queensland Department of Environment and Science’s Koala Habitat Suitability Model (HSM) within the South East Queensland Regional Plan area used a categorised Maxent model output (based on key biophysical variables with a statistically tested relationship to koalas) in combination with an expert derived Regional Ecosystem (RE) classification and koala occurrence records. The model used a set of decision rules (matrix) to determine which areas are considered ‘core’, ‘non-core’ and ‘non-habitat’. For detailed information relating to the methodology and rule set employed to delineate Phascolarctos cinereus (koala) habitat within the SEQ Regional Plan area, refer to the accompanying report (DES, 2020) available from the Department of Environment and Science’s Biodiversity Assessment Team – biodiversity.planning@des.qld.gov.au.
Restoration areas were identified using a Marxan scenario that considered important areas to restore habitat based on a draft koala HSM and to attribute an ecological cost to threat, constraint, opportunity and resilience modelling to identify preferred restoration areas. The Marxan scenario targeted cleared areas within the Koala HSM matrix rulesets 351, 350, 341 and 340 (all areas ranked high on the Maxent and ranked high or very high for Regional Ecosystem). Please note that non-target land uses (e.g. lakes, roads, dwellings) that have occurred since the clearing of regional ecosystems were not been removed from this layer. After feedback from local government, further refinement removed areas in the mapping where restoration was considered unsuitable in certain planning scheme zones or areas (such as urban areas including residential, centres, industrial and related infrastructure). However, relevant areas were retained where an environmental corridor (or biodiversity area) was present.
<DIV STYLE="text-align:Left;"><DIV><DIV><P><SPAN><SPAN>While every care is taken to ensure the accuracy of this information, the Department of Environment and Science makes no representations or warranties about its accuracy, reliability, completeness or suitability for any particular purpose and disclaims all responsibility and all liability (including without limitation, liability in negligence) for all expenses, losses, damages (including indirect or consequential damage) and costs which might be incurred as a result of the information being inaccurate or incomplete in any way and for any reason.</SPAN></SPAN></P></DIV></DIV></DIV>
Manager, Koala Policy and Oversight
Department of Environment and Science
Manager, Koala Policy and Oversight
GPO Box 2454,
Brisbane
Queensland
4001
SEQKoalaStrategy@des.qld.gov.au
AU
Manager, Koala Policy and Oversight
Manager, Koala Policy and Oversight
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KHRA
Koala Habitat Restoration Area
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separates restoration areas into those
-in a Koala Priority Area ('Koala Habitat Restoration Areas – Koala Priority Areas'), or
-not in a Koala Priority Area ('Koala Habitat Restoration Areas')
Department of Environment and Science
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Koala Priority Area
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indicates restoration areas inside Koala Priority Areas and those outside Koala Priority Areas
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The KPA restoration areas were within the following area: South East Queensland Regional Planning area 2017.
Within the overall HSM extent, the completeness of the assessment cannot be quantified. Completeness of the modelled output with respect to delineating on ground habitat and confidence of occurrence, for example, is dependent upon known observations of the species (rather than the species “true” on ground distribution), expert interpretation in terms of the species habitat preference (based upon available knowledge at the time) and the completeness of base dataset inputs (i.e. the Queensland Herbarium’s regional ecosystem mapping product).
All polygons relevant to habitat have a Habitat Value Category (HSM_VALUE) and Confidence Level (HSM_CONF) based on the rule sets described in the relevant taxon profile.
The base spatial unit used in this model was derived from the Regional Ecosystem mapping. Refer to the Queensland Herbarium for further information on spatial accuracies associated with the regional ecosystem mapping product.
A “ground truthing” assessment to assess attribute and predictive accuracy of this product has not been performed at this stage. The product and its associated attribution are largely dependent upon the underlying base datasets used in its development. For example, attributional accuracy is in part dependent upon regional ecosystem information (as well as expert categorisation) to infer preferred habitat. Contact the relevant custodians for further information on the base data inputs used (as listed in the section titled “Lineage”).
The restoration mapping (KHRA) was produced by the Department of Environment and Science staff based upon the methodology set out in the report (DES, 2020). For specific information relating to the methodology and rule set employed to delineate Phascolarctos cinereus (koala) habitat restoration areas, refer to the accompanying documentation (available from the Department of Environment and Science’s Biodiversity Assessment Team – biodiversity.planning@des.qld.gov.au). Polygon slivers with an area of less than 0.25 hectares and pinch points of 1 metre or less have been removed from this dataset.
Source data: The following key base data sets were used in production of KHRA:
1. The Koala Habitat Suitability Model v1.0 developed by the Department of Environment and Science.
2. Koala Priority Areas (KPAs) v1.0 developed by the Department of Environment and Science.
3. DES’s Marxan output scenario 208 – run 3 Target 90,000 ha of former habitat on matrix rules 351, 350, 341 and 340 within KPA areas. The ecological cost layer included roads, heat stress, climate change, urban development, extractive industries, conservation management zones, current koala bushland habitat in PKADAs and KADAs, and resilience refugia. NB for further information on the base inputs used to develop the Marxan scenario, refer to DES accompanying documentation.
4. Zoning and environmental data for the suitable area refinement was acquired through local government directly or open data in September 2019. Regional biodiversity corridors under the Shaping SEQ Regional Plan were also acquired and Department provided koala restoration properties. Zones and precincts were interpreted to zones under the Planning Regulation 2017. Ranking was applied to the zoning and environment corridor data to apply the restoration areas only to “potentially suitable zones”, “environment corridors” or “existing koala restoration areas”. The final areas were refined to identify "potentially suitable areas" and "potentially unsuitable areas".
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Manager, Koala Policy and Oversight
Department of Environment and Science
Manager, Koala Policy and Oversight
GPO Box 2454,
Brisbane
Queensland
4001
SEQKoalaStrategy@des.qld.gov.au
AU
Manager, Koala Policy and Oversight
Manager, Koala Policy and Oversight
Manager, Koala Policy and Oversight
Department of Environment and Science
Manager, Koala Policy and Oversight
GPO Box 2454,
Brisbane
Queensland
4001
SEQKoalaStrategy@des.qld.gov.au
AU
Manager, Koala Policy and Oversight
Manager, Koala Policy and Oversight
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