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14562800
1.0
ISO 19139 Metadata Implementation Specification
FALSE
HSM_SEQRP_KOALA
151.767524
153.544682
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Geographic
GCS_GDA_1994
Angular Unit: Degree (0.017453)
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ISO19139
7CE3AF11-0FE0-4C0C-8925-12E6BEF46F4D
Manager, Biodiversity Assessment
Department of Environment and Science
Manager, Biodiversity Assessment
biodiversity.planning@des.qld.gov.au
13 74 68
Manager, Biodiversity Assessment
Manager, Biodiversity Assessment
ESRI 10.3
Feature Class
2020-01-20T00:00:00
Version 1.0
Manager, Biodiversity Assessment
Department of Environment and Science
Manager, Biodiversity Assessment
biodiversity.planning@des.qld.gov.au
13 74 68
Manager, Biodiversity Assessment
Phascolarctos cinereus (Koala) Habitat Areas (KHA) – South East Queensland Regional Plan (SEQRP): remnant and regrowth, core habitat, v1.0
20200120
Manager, Biodiversity Assessment
Department of Environment and Science
Manager, Biodiversity Assessment
biodiversity.planning@des.qld.gov.au
13 74 68
Manager, Biodiversity Assessment
Manager, Biodiversity Assessment
Manager, Biodiversity Assessment
Phascolarctos cinereus (koala) Habitat Suitability Model delineating core habitat for the species across remnant and regrowth vegetation.
© State of Queensland (Department of Environment and Science), 2020
Queensland
Phascolarctos cinereus
Koala
Threatened species habitat
Habitat modelling
FAUNA Native
ECOLOGY Habitat
ECOLOGY Models
The Habitat Suitability Model framework employed by the Queensland Department of Environment and Science’s Biodiversity Assessment Team aims to determine the known extent, possible extent and importance of habitat for threatened taxa listed under Queensland and/or Australian government legislation and for priority taxa listed during bioregional/catchment assessments. The approach shifts the conservation focus away from specific point locations (sites of taxa presence based on historic records) in the landscape to areas where the taxon is known to occur, or is likely to occur. The habitat model aims to be consistent, repeatable and transparent, documenting reasons for a particular level of assessment. It is conducted irrespective of tenure or the significance of areas for other conservation reasons.
To produce a comprehensive map and identify important areas of koala habitat within the South East Queensland Regional Plan (SEQRP) area, the modelling approach integrated a species distribution model with the Queensland Herbarium’s regional ecosystem (RE) mapping and koala occurrence records. The modelling approach 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 classification and validated koala occurrence records.
The koala habitat mapping was created using a koala habitat decision matrix to integrate the categorised output from a species distribution model (created using Maxent) with a regional ecosystem suitability classification and buffered koala records. The decision matrix established the rules for categorising known habitat and possible habitat and for designating core habitat, non-core habitat and non-habitat. Koala occurrence records, buffered by 900m, were used to confirm the likelihood of koala habitat.
Known habitat was assigned where suitable regional ecosystems were confirmed by the presence of a koala record – indicating areas where koalas are known to occur.
Possible habitat was assigned where there was an absence of a koala record in a polygon with a suitable regional ecosystems – indicating areas where koalas are likely to occur.
The 30 rules from the koala habitat decision matrix were grouped into 10 categories, from lowest suitability (rank 1) to highest suitability (rank 10). Only core habitat (matrix categories 4 to 10) were included in model release version 1.0:
Core habitat – matrix categories 4 to 10
Core habitat refers to the best habitat for koalas, based on the combination of biophysical measures, suitable vegetation and koala occurrence records. Core habitat was delineated where there was agreement between the regional ecosystems ranked high, medium or low suitability by the Koala Advisory Group (KAG) and Maxent areas ranked high or medium (with or without a koala record).
For detailed information relating to the methodology and rule set employed to delineate Phascolarctos cinereus (koala) habitat within the SEQ Regional Planning 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.
* Maxent is a commonly used statistical tool for species distribution modelling, using presence only data.
Manager, Biodiversity Assessment
Department of Environment and Science
Manager, Biodiversity Assessment
GPO Box 2454, City, Brisbane
Brisbane
Queensland
4001
biodiversity.planning@des.qld.gov.au
13 74 68
DES (2019a). Spatial modelling and planning for koalas in SEQ: Report. Brisbane: Department of Environment and Heritage Protection, Queensland.
DES (2019b). Spatial modelling and planning for koalas in SEQ: GIS Technical Document. Brisbane: Department of Environment and Heritage Protection, Queensland.
<DIV STYLE="text-align:Left;"><DIV><DIV><P STYLE="margin:0 0 0 0;"><SPAN>This dataset is provided for information purposes only. In reports, maps and metadata for products derived from this coverage, the following acknowledgement is required: ©State of Queensland (Department of Environment and Science), 20</SPAN><SPAN>20</SPAN><SPAN /></P></DIV></DIV></DIV>
<DIV STYLE="text-align:Left;"><DIV><DIV><P STYLE="margin:0 0 11 0;"><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></P><P><SPAN /></P></DIV></DIV></DIV>
<DIV STYLE="text-align:Left;"><DIV><DIV><P STYLE="margin:0 0 0 0;"><SPAN><SPAN>The </SPAN></SPAN><SPAN STYLE="font-style:italic;"><SPAN>Phascolarctos cinereus </SPAN></SPAN><SPAN><SPAN>(Koala) Habitat Suitability Model (HSM) provides the delineation of core habitat for the species and includes a representation of known and potential habitat. Core habitat is designated using rules defined by experts and through a modelling process. Habitat suitability models (HSM) may be used to inform planning decisions, Biodiversity Planning Assessments (BPAs), Aquatic Conservation Assessments (ACAs) and Essential Habitat under the </SPAN></SPAN><SPAN STYLE="font-style:italic;"><SPAN>Vegetation Management Act 1999</SPAN></SPAN><SPAN><SPAN>. </SPAN></SPAN></P><P STYLE="margin:0 0 11 0;"><SPAN /></P></DIV></DIV></DIV>
0
151.767524
153.544682
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-28.363832
Version 6.2 (Build 9200) ; Esri ArcGIS 10.7.1.11595
Manager, Biodiversity Assessment
Department of Environment and Science
Manager, Biodiversity Assessment
biodiversity.planning@des.qld.gov.au
13 74 68
Manager, Biodiversity Assessment
Manager, Biodiversity Assessment
The Phascolarctos cinereus (koala) Habitat Suitability Model (HSM) was produced by Department of Environment and Science staff based upon the methodology as set out in the report (DES, 2020). For specific information relating to the methodology and rule set employed to delineate Phascolarctos cinereus (koala) habitat, refer to the accompanying documentation (available from the Department of Environment and Science’s Biodiversity Assessment Team – biodiversity.planning@des.qld.gov.au). Polygons with an area of less than 0.25 hectares. Polygon slivers with pinch points of 1 metre or less have been removed from this dataset.
HSM SEQRP release version 1.0 incorporates the following key features: 1. Study area aligns with ShapingSEQ: South East Queensland Regional Plan 2017 boundary
2. Regional ecosystem version 11 (2018), update provided January 2020
3. High value regrowth (November, 2019). update provided January 2020
4. Core defined by 12 rules (matrix categories 4–10)
5. Island habitat excluded, except for three islands (North Stradbroke Island, South Stradbroke Island and Bribie Island)
6. Koala records v3.0, (January 2020)
7. PMAV Category X areas (dated 17/12/2019) erased
7. Submitted for release 20 January 2020
Source data: The following key base data sets were used in production of this HSM:
1. The base spatial unit was the regional ecosystem mapping for Queensland version 11 (2018). Queensland Herbarium, Department of Environment and Science.
2. Koala records were collated specifically for the project through a variety of sources, including consultation with local governments and other groups, DES systematic survey data, koalaBase and Atlas of Living Australia. Additional records provided by local governments were incorporated into this version of the model (January 2020)
3. High Value Regrowth mapping (November 2019). Queensland Herbarium, Department of Environment and Science.
4. Categorised Maxent output 11.17 (version 1.1, 2017), Biodiversity Assessment Team, Department of Environment and Science. Nb., the 11.17 model was extrapolated to areas newly incorporated into the study area due to boundary changes in the ShapingSEQ: South East Queensland Regional Plan 2017. 5. Regional ecosystem erase layer produced by the Department of Environment and Science, Queensland Herbarium. 13 January 2020.
5. High Value regrowth erase layer produced by the Department of Environment and Science, Queensland Herbarium. 13 January 2020.
7. For further information on the base inputs and methodology, refer to the report “Spatial Modelling and Planning for Koalas (SMPK) in southern SEQ” (DES 2019a); and GIS technical document (DES 2019b) available from the Department of Environment and Science’s Biodiversity Assessment Team – biodiversity.planning@des.qld.gov.au.
South East Queensland Regional Plan 2017 (ShapingSEQ - 2017)
The HSM encapsulated the following area: South East Queensland Regional Plan 2017 (ShapingSEQ - 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 adhere to the rules established by the decision matrix to designate core habitat, non-core habitat and non-habitat (HSM_CORE) and to identify habitat where the species is known to occur (habitat known) or is likely to occur (habitat possible) (HSM_VALUE).
Absolute external positional accuracy: The base spatial unit used in this model was 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). Maxent rankings were attributed to regional ecosystem polygons using logistic values from the model output categorised into three classes based on a high threshold (maximum sum of sensitivity and specificity–maxSSS) and a low threshold (10th percentile training presence–P10). The translation of raster Maxent values into vector regional ecosystem polygons was achieved using a 20% allocation threshold, so that each regional ecosystem polygon was populated with the highest Maxent ranked component that occupied 20% or more of that polygon. For example, a regional ecosystem polygon that consisted of 20% high and 80% low Maxent ranked components would be categorised as high Maxent rank. Koala presence was attributed to regional ecosystem polygons using a 900m point buffer intersect. Assignment of all attributes to the regional ecosystem polygons was fully automated using Python scripting based on decision matrix rules.
Contact the relevant custodians for further information on the base data inputs used (as listed in the section titled “Lineage”).
HSM_SEQRP_KOALA
Feature Class
65407
The spatial entity type is the value stored in the entity member field of the geometry object.
Esri
OBJECTID
OBJECTID
OID
4
10
0
Internal feature number.
Esri
Sequential unique whole numbers that are automatically generated.
Shape
SHAPE
Geometry
4
0
0
Feature geometry.
Esri
Coordinates defining the features.
RE
Regional ecosystem
String
50
0
0
The regional ecosystem represents a vegetation community in a bioregion that is consistently associated with a particular combination of geology, landform and soil. A maximum of five vegetation units (RE1–RE5) may be attributed in a heterogeneous polygon (polygons with more than one regional ecosystem occurring in them). Values: Regional ecosystem identifiers (e.g. 12.11.5 or 12.11.5/12.3.3).
Queensland Herbarium v.11.0 Regional Ecosystem Mapping
PERCENT
RE percent
String
14
0
0
Proportional area (%) of each regional ecosystem (i.e. RE1 to RE5) with respect to the polygon area. Values: 5–100 (e.g. 5 or 95/5)
Queensland Herbarium v.11.0 Regional Ecosystem Mapping
RE_VERSION
RE version
String
50
0
0
Regional Ecosystem mapping version
Queensland Herbarium v.11.0 Regional Ecosystem Mapping
AREA_HA
Area (hectares)
Double
8
38
8
Area in hectares calculated using MGA Zone 56 coordinates
Department of Environment and Science
MRE_RANK_ALL
Model RE suitability ranking list
String
254
0
0
Lists the koala suitability rank for each RE in a polygon. Values: s1 = non-habitat; s2 = very low; s3 = low; s4 = medium; s5 = high (e.g. s4/s5 means a heterogeneous polygon containing REs ranked medium (s4) and high (s5).
Department of Environment and Science
MRE_RANK
Model RE suitability rank
String
254
0
0
Final RE species habitat suitability rank (words). Values: high, medium, low, very low, non-habitat.
Department of Environment and Science
MRE_PROPTOT_ALL
Model RE proportion list
String
50
0
0
Lists all RE koala suitability proportions for each of the five regional ecosystem rankings (i.e rank1/rank2/rank3/rank4/rank5) with respect to the polygon area. Values: range from 0–100 separated by a slash.
Department of Environment and Science
MME_RANK
Model Maxent rank
String
50
0
0
Final Maxent species habitat suitability rank
Department of Environment and Science
MME_PROPTOT_ALL
Model Maxent proportion list
String
50
0
0
Lists all Maxent proportions
Department of Environment and Science
PT_BUFF
Species record buffer
SmallInteger
2
5
0
Species point record buffer presence. Values: 1 (presence), 0 (absence)
Department of Environment and Science
HSM_VER
Habitat model version
String
20
0
0
Habitat suitability model version
Department of Environment and Science
SCI_NAME
Scientific name
String
250
0
0
Scientific name of the species. Values: Phascolarctos cinereus.
Department of Environment and Science
HSM_CODE
Species code
String
10
0
0
Habitat suitability model species code. Values: phascine.
Department of Environment and Science
HSM_VALUE
Habitat value
String
30
0
0
Habitat suitability model habitat value. Values: Preferred habitat known, Preferred habitat possible, General habitat known, General habitat possible, Non-habitat.
Department of Environment and Science
HSM_CONF
Model confidence
String
20
0
0
Model confidence based on the rule sets in the taxon profile
Department of Environment and Science
HSM_CORE
Core habitat
String
20
0
0
Habitat suitability model core habitat (Core)
Department of Environment and Science
HSM_RULE
Habitat model decision rule
String
15
0
0
Habitat suitability model matrix decision rule
Department of Environment and Science
HSM_RULE_ALL
Habitat model decision rule list
String
100
0
0
Lists all rules matching decision matrix criteria
Department of Environment and Science
MCOVER
Model vegetation cover
String
20
0
0
Describes the cover status of the vegetation, for example, pre-clearing, remnant, regrowth. Values: Remnant, Regrowth.
Department of Environment and Science
SE_ANNO_CAD_DATA
SE_ANNO_CAD_DATA
Blob
0
0
0
HSM_CATEGORY
Habitat suitability category
SmallInteger
2
5
0
Habitat suitability category ranks the suitability of koala habitat from lowest koala habitat suitability (category 1) to highest koala habitat suitability (category 10) using rules from the habitat decision matrix. Values: 1–10.
Categories 4–10 represent core habitat as follows: category 10 = rules 351, 350; category 9 = rules 341, 340; category 8 = rules 331, 330; category 7 = rule 251; category 6 = rule 241; category 5 = rule 231; category 4 = rules 250, 240, 230. Categories 2–3 represent non-core habitat as follows: category 3 non-core (rainforest habitat) = rules 321, 320, 221, 220, 121;
category 2 non-core (marginal habitat) = rules 151, 150, 141, 140, 131, 130.
Category 1 represents non-habitat as follows: category 1 non-habitat = rules 311, 310, 211, 210, 111,110, 120.
Department of Environment and Science
SHAPE.AREA
SHAPE.AREA
Double
0
0
0
SHAPE.LEN
SHAPE.LEN
Double
0
0
0
dataset
EPSG
8.3.4(3.0.1)
65407
Simple
FALSE
65407
TRUE
FALSE
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