20191129 15525000 1.0 ISO 19139 Metadata Implementation Specification FALSE seq_regionalplan_2017_rbv 151.767524 153.546706 -28.363832 -26.137121 1 002 Geographic GCS_GDA_1994 Angular Unit: Degree (0.017453) <GeographicCoordinateSystem xsi:type='typens:GeographicCoordinateSystem' xmlns:xsi='http://www.w3.org/2001/XMLSchema-instance' xmlns:xs='http://www.w3.org/2001/XMLSchema' xmlns:typens='http://www.esri.com/schemas/ArcGIS/3.5.0'><WKT>GEOGCS[&quot;GCS_GDA_1994&quot;,DATUM[&quot;D_GDA_1994&quot;,SPHEROID[&quot;GRS_1980&quot;,6378137.0,298.257222101]],PRIMEM[&quot;Greenwich&quot;,0.0],UNIT[&quot;Degree&quot;,0.0174532925199433],AUTHORITY[&quot;EPSG&quot;,4283]]</WKT><XOrigin>-400</XOrigin><YOrigin>-400</YOrigin><XYScale>999999999.99999988</XYScale><ZOrigin>-100000</ZOrigin><ZScale>10000</ZScale><MOrigin>-100000</MOrigin><MScale>10000</MScale><XYTolerance>8.98315284119521e-09</XYTolerance><ZTolerance>0.001</ZTolerance><MTolerance>0.001</MTolerance><HighPrecision>true</HighPrecision><LeftLongitude>-180</LeftLongitude><WKID>4283</WKID><LatestWKID>4283</LatestWKID></GeographicCoordinateSystem> 20260401 23363700 20260401 23363700 ISO19139 500000 50000 dataset Queensland Herbarium, DSITI Brisbane Botanic Gardens, Mt Coot-tha Road Toowong QLD 4066 Queensland.Herbarium@dsitia.qld.gov.au Australia 61 7 3896 9326 20260401 10 Enterprise Geodatabase Feature Class 162.311 SEQ regional biodiversity value Dr Gordon Guymer Queensland Herbarium, DSITI Director Brisbane Botanic Gardens, Mt Coot-tha Road TOOWONG QLD 4066 Queensland.Herbarium@dsitia.qld.gov.au Australia 61 7 3896 9326 61 7 3896 9624 9 am - 5 pm CITATION: Queensland Herbarium (2015) Biodiversity Status of 2013 Remnant Regional Ecosystems of Queensland, Version 9.0 (April 2015) (Department of Science, Information Technology and Innovation: Brisbane). 2000-07-19T00:00:00 2015-03-02T00:00:00 Version 9.0 QUEENSLAND Department of State Development, Infrastructure, Local Government and Planning (DSDILGP) 2023. <DIV STYLE="text-align:Left;"><P STYLE="margin:0 0 11 0;"><SPAN>To the extent permitted by law, The Department of State Development, Infrastructure, Local Government and Planning (DSDILGP) gives no warranty in relation to the material or information contained in this data (including accuracy, reliability, completeness or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including indirect or consequential damage) relating to any use of the material or information contained in this Data; and responsibility or liability for any loss or damage arising from its use. </SPAN></P></DIV> Regional biodiversity values have been mapped in SEQ and identify: - large tracts of vegetation - aquatic connectivity - areas of species richness and diversity - areas of ecosystem representation and uniqueness - climate adaptation zones and refugia. Data remains unchanged for ShapingSEQ 2023. SEQ Regional Plan South East Queensland ShapingSEQ Regional Biodiversity Values QUEENSLAND Dr Gordon Guymer Queensland Herbarium Director Brisbane Botanic Gardens, Mt Coot-tha Road TOOWONG QLD 4066 Queensland.Herbarium@science.dsitia.qld.gov.au Australia 61 7 3896 9326 61 7 3896 9624 http://dds.information.qld.gov.au/dds/ Biennial release The State of Queensland (Department of Science, Information Technology and Innovation) 2015. While every care is taken to ensure the accuracy of the Information Product, the Department of Science, Information Technology and Innovation 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 you might incur as a result of the product being inaccurate or incomplete in any way and for any reason. Esri ArcGIS 13.5.3.57366 1 151.767524 153.546706 -26.137121 -28.363832 <DIV STYLE="text-align:Left;"><DIV><DIV><P><SPAN STYLE="font-size:9pt">Regional biodiversity values have been mapped in SEQ and identify:</SPAN></P><P><SPAN STYLE="font-size:9pt">- large tracts of vegetation</SPAN></P><P><SPAN STYLE="font-size:9pt">- aquatic connectivity</SPAN></P><P><SPAN STYLE="font-size:9pt">- areas of species richness and diversity</SPAN></P><P><SPAN STYLE="font-size:9pt">- areas of ecosystem representation and uniqueness</SPAN></P><P><SPAN STYLE="font-size:9pt">- climate adaptation zones and refugia.</SPAN></P><P><SPAN /></P><P><SPAN STYLE="font-size:9pt">These values are critical at a regional level to enable the protection of interacting ecosystem functions and their associated species and diversity. These values are to be investigated and refined by local government for protection as matters of local environment significance (MLES). This is in addition to protecting those areas identified as having MSES. These areas are important as they contribute to an ecologically sound and resilient regional network of habitats and corridors.</SPAN></P><P><SPAN /></P></DIV></DIV></DIV> Biennially General Source Data: 1:80,000 B&W 1960’s aerial photography, Landsat TM imagery rectified to 1:100,000 topographic maps, geology, soils and land systems data, topographic maps, field survey, existing field site data and existing mapped data (digital and hard-copy). Other reference data: National Estates (QLD), DCDB. Primary data source for the Wet Tropics bioregion 1:50,000 scale regional ecosystem mapping: • Vegetation of the Wet Tropics of Queensland bioregion. Wet Tropics Management Authority, Cairns, Stanton J.P. and Stanton, D.J. (2005). Additional Source Data for SEQ 1:50,000 scale mapping: 1:100,000 scale geological mapping NR&M (2002) and extensive field data for all revisions. • Ipswich, Mt Lindesay, Esk & Helidon sheets revised (2000-2001) using 1:25,000 colour aerial photography (1994-1997). • Gatton Shire revision using 1:25,000 colour aerial photography (1997) and Gatton Shire Remnant vegetation mapping, QPWS, Grimshaw (2001). • Crows Nest Shire revision using 1:25,000 colour aerial photography (2000). • Boonah Shire revision using 1:25,000 vegetation survey, Olsen (2001). • Laidley Shire revision using 1:25,000 colour aerial photography (1997) and 1:50,000 vegetation survey, Lockyer Landcare (1997). • Noosa Shire revision using 1:25,000 colour aerial photography (1997 & 2000) and Noosa Shire 1:25,000 vegetation survey, Burrows (2000). • Pine Rivers Shire revision using 1:25,000 colour aerial photography (1997), Pine Rivers Shire regional ecosystem database (2001) and the Brisbane Forest Park, 1:25,000 vegetation survey, Young (1996). • Logan City revision using 1:25,000 Logan City vegetation survey, Ecograph (2000). • Redland Shire revision using 1:25,000 Redland Shire vegetation survey, Olsen (2001). • Gold Coast City Council revision using 1:10,000 digital ortho-photography (2001) and QPWS Fire Management Strategy (2001). • Beaudesert Shire revision using 1:25,000 colour aerial photography (1997) and Beaudesert Shire vegetation survey, Chenoweth EPLA (2002) and QPWS Fire Management Strategy (2001). • Cooloola Shire revision using 1:40,000 colour aerial photography (1996) and Cooloola Shire vegetation survey, Lowe (2002). • Maroochy Shire revision using 1:25,000 colour aerial photography (1997) and Maroochy Shire vegetation survey, MSC (2002). • Caloundra City Council revision using 1:25,000 colour aerial photography (1997). The pre-clearing vegetation is simply the vegetation before clearing. Mapping of pre-clearing vegetation is based on the interpretation of landscape as depicted on aerial photos or satellite imagery (Landsat, Spot), and ground truthed on a limited sample of known points. The Queensland Herbarium uses the 1:80,000 black and white 1960’s photos as the standard imagery for mapping pre-clearing vegetation. The structural classification system is based on Walker and Hopkins (1990). Where vegetation has already been cleared on these aerial photographs, the pre-clearing vegetation is reconstructed by the botanist using available information, including landform, soils, geology, field data (remnant roadside trees) and ecological knowledge. In addition, historical survey records of vegetation types and older aerial photos (if they exist) are used extensively in this reconstruction. The 2013 extent is based on the 2013 extent mapping that was derived from the standard state-wide coverage of dry season (around September) 2013. Technical processes: Vegetation boundaries are drawn on aerial photographs and manually digitised. Boundaries are referenced primarily to rectified Landsat imagery (SLATS, DSITI) and to orthophotos if available. Field survey provided partial verification of boundaries. Pre-clearing vegetation is delineated using above resource material. Remnant vegetation boundaries derived by intersecting the ‘vegetation cover’ with the pre-clear coverage and altering attributes to reflect the remaining vegetation components of each polygon. The vegetation cover data is generated from Landsat imagery, using change detection data &/or Foliage Protection Cover (woody cover) from SLATS, DSITI, as additional indicators of remnant, cleared or disturbed areas. Related polygon coverages include: pre-clearing vegetation communities and regional ecosystems, 1997, 1999, 2000, 2001, 2003, 2005, 2006, 2006b, 2009, 2011 remnant regional ecosystems and, for areas where regional ecosystem coverages have not been completed, a separate polygon layer, vegetation cover (e.g.: remcov13). Polygons 100m; Sites +/- 10m. Positional accuracy of polygons is noted in the field 'L', which is a reliability code and given as either A, B or C for high, moderate and low confidence in accuracy of polygon boundaries. The level is determined on the basis of the reliability of interpretation of photopattern /reflectance of remotely sensed data (aerial photographs and rectified Landsat TM imagery) and on the positioning and frequency of sites and traverses. Reliability code is contained in the field 'V' which refer to vegetation attributes - RE (regional ecosystem) and PERCENT accuracy and given as either A, B or C for high, moderate and low confidence in accuracy of polygon attributes. Logical consistency has been determined through the following: All polygons visually checked at 1:100,000 scale and by topological consistency checks. A test of consistency for regional ecosystem unit values (RE and PERCENT) between the pre-clearing and remnant coverages. 97 EPSG 6.5(3.0.1) seq_regionalplan_2017_rbv Feature Class 97 OBJECTID objectid OID 4 10 0 Internal feature number. Esri Sequential unique whole numbers that are automatically generated. Shape shape Geometry 8 0 0 Feature geometry. ESRI Coordinates defining the features. Shape_Leng shape_leng Double 8 38 8 AREA_HA area_ha Double 8 38 8 Name name String 50 0 0 st_area(shape) st_area(shape) Double 0 0 0 st_perimeter(shape) st_perimeter(shape) Double 0 0 0 Simple FALSE 97 FALSE FALSE