Changes
On May 16, 2022 at 12:36:01 PM +1000, National Native Title Tribunal:
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Removed the source URL from Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Changed value of field
temporal_coverage_from
to2016-10-01
in Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate -
Added resource Native Forestry Map Viewer to Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Added resource Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate to Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Added resource Operational Map for River-Flat Eucalypt Forest Threatened Ecological Community on NSW Crown Forest Estate to Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Added resource Data Quality Statement to Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Added resource Operational and Indicative Maps for the Assessment of Threatened Ecological Communities on NSW Crown Forest Estate to Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Deleted resource Operational and Indicative Maps for the Assessment of Threatened Ecological Communities on NSW Crown Forest Estate from Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Deleted resource Data Quality Statement from Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Deleted resource Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate from Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Deleted resource Native Forestry Map Viewer from Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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Deleted resource Operational Map for River-Flat Eucalypt Forest Threatened Ecological Community on NSW Crown Forest Estate from Assessment of River-Flat Eucalypt forest on Coastal floodplains TEC on NSW Crown Forest Estate
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6 | "key": "harvest_portal", | 6 | "key": "harvest_portal", | ||
7 | "value": "SEED" | 7 | "value": "SEED" | ||
8 | }, | 8 | }, | ||
9 | { | 9 | { | ||
10 | "key": "harvest_url", | 10 | "key": "harvest_url", | ||
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12 | nsw.gov.au/dataset/assessment-of-river-flat-eucalypt-forest-tec-south" | 12 | nsw.gov.au/dataset/assessment-of-river-flat-eucalypt-forest-tec-south" | ||
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19 | "license_title": "Creative Commons Attribution", | 19 | "license_title": "Creative Commons Attribution", | ||
20 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 20 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
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24 | "metadata_created": "2018-06-15T08:52:48.772839", | 24 | "metadata_created": "2018-06-15T08:52:48.772839", | ||
n | 25 | "metadata_modified": "2021-09-06T23:31:37.578928", | n | 25 | "metadata_modified": "2022-05-16T02:36:01.034249", |
26 | "name": "assessment-of-river-flat-eucalypt-forest-tec-south", | 26 | "name": "assessment-of-river-flat-eucalypt-forest-tec-south", | ||
27 | "notes": "The operational map for River-flat Eucalypt Forest (RFEF) | 27 | "notes": "The operational map for River-flat Eucalypt Forest (RFEF) | ||
28 | was constructed to resolve long-standing issues surrounding its | 28 | was constructed to resolve long-standing issues surrounding its | ||
29 | identification, location and extent within the NSW State Forest estate | 29 | identification, location and extent within the NSW State Forest estate | ||
30 | covered by the coastal Integrated Forestry Operation Agreements. The | 30 | covered by the coastal Integrated Forestry Operation Agreements. The | ||
31 | map was constructed in two parts, with State Forests to the north of | 31 | map was constructed in two parts, with State Forests to the north of | ||
32 | Sydney being mapped in a separate process to those to the south of | 32 | Sydney being mapped in a separate process to those to the south of | ||
33 | Sydney. We did this to minimise the risk that relationships between | 33 | Sydney. We did this to minimise the risk that relationships between | ||
34 | regional vegetation communities and the TEC would be confounded or | 34 | regional vegetation communities and the TEC would be confounded or | ||
35 | masked by geographical variation or other major ecological gradients, | 35 | masked by geographical variation or other major ecological gradients, | ||
36 | which might otherwise be a significant risk if we had treated the full | 36 | which might otherwise be a significant risk if we had treated the full | ||
37 | latitudinal range of the TEC as a single study area. In total, we | 37 | latitudinal range of the TEC as a single study area. In total, we | ||
38 | assessed 1,218,000 hectares of State Forest across coastal NSW. This | 38 | assessed 1,218,000 hectares of State Forest across coastal NSW. This | ||
39 | consisted of 868,000 hectares of State Forest on the north coast and | 39 | consisted of 868,000 hectares of State Forest on the north coast and | ||
40 | more than 350,000 hectares of State Forest on the south coast. \r\nIn | 40 | more than 350,000 hectares of State Forest on the south coast. \r\nIn | ||
41 | both study areas, the project\u2019s Threatened Ecological Community | 41 | both study areas, the project\u2019s Threatened Ecological Community | ||
42 | (TEC) Reference Panel (the Panel) preceded the assessment process by | 42 | (TEC) Reference Panel (the Panel) preceded the assessment process by | ||
43 | reviewing the determination for RFEF and agreeing upon a set of | 43 | reviewing the determination for RFEF and agreeing upon a set of | ||
44 | diagnostic parameters for its identification. The Panel found that | 44 | diagnostic parameters for its identification. The Panel found that | ||
45 | RFEF is primarily defined by floristic plot data and that it is mostly | 45 | RFEF is primarily defined by floristic plot data and that it is mostly | ||
46 | located on coastal floodplains and associated alluvial | 46 | located on coastal floodplains and associated alluvial | ||
47 | landforms.\r\nFollowing on from these conclusions, we started the | 47 | landforms.\r\nFollowing on from these conclusions, we started the | ||
48 | mapping process by mapping the distribution of floodplains and | 48 | mapping process by mapping the distribution of floodplains and | ||
49 | alluvial soils and thus identifying possible areas of RFEF. For both | 49 | alluvial soils and thus identifying possible areas of RFEF. For both | ||
50 | the north and the south coast we used an existing map of coastal | 50 | the north and the south coast we used an existing map of coastal | ||
51 | landforms and geology in combination with several fine-scale models of | 51 | landforms and geology in combination with several fine-scale models of | ||
52 | alluvial landform features to determine the likely extent of | 52 | alluvial landform features to determine the likely extent of | ||
53 | floodplains and alluvial soils within our study areas.\r\nWe used | 53 | floodplains and alluvial soils within our study areas.\r\nWe used | ||
54 | aerial photograph interpretation (API) to assess the floristic and | 54 | aerial photograph interpretation (API) to assess the floristic and | ||
55 | structural attributes of the vegetation cover found on our modelled | 55 | structural attributes of the vegetation cover found on our modelled | ||
56 | alluvial environments, and thus delineated polygons likely to contain | 56 | alluvial environments, and thus delineated polygons likely to contain | ||
57 | RFEF. We also used API to modify the boundaries of the modelled | 57 | RFEF. We also used API to modify the boundaries of the modelled | ||
58 | alluvial areas using a prescribed list of eucalypt, casuarina and | 58 | alluvial areas using a prescribed list of eucalypt, casuarina and | ||
59 | melaleuca species in combination with the interpretation of landform | 59 | melaleuca species in combination with the interpretation of landform | ||
60 | elements relevant to alluvial and floodplain environments.\r\nWe then | 60 | elements relevant to alluvial and floodplain environments.\r\nWe then | ||
61 | compiled floristic plot data for all State Forest areas within our | 61 | compiled floristic plot data for all State Forest areas within our | ||
62 | modelled alluvial landforms and API polygons. For both the north and | 62 | modelled alluvial landforms and API polygons. For both the north and | ||
63 | the south coast the floristic plot data was sourced from both existing | 63 | the south coast the floristic plot data was sourced from both existing | ||
64 | flora surveys held in the OEH VIS database and from targeted flora | 64 | flora surveys held in the OEH VIS database and from targeted flora | ||
65 | surveys conducted specifically for this project. We compared these | 65 | surveys conducted specifically for this project. We compared these | ||
66 | plots with those previously assigned to flora communities listed in | 66 | plots with those previously assigned to flora communities listed in | ||
67 | the determination of RFEF. Both dissimilarity-based methods and | 67 | the determination of RFEF. Both dissimilarity-based methods and | ||
68 | multivariate regression methods were used for the comparison. The | 68 | multivariate regression methods were used for the comparison. The | ||
69 | results of the comparison were then used to assess the likelihood that | 69 | results of the comparison were then used to assess the likelihood that | ||
70 | the plots in State forests belonged to one or more of the communities | 70 | the plots in State forests belonged to one or more of the communities | ||
71 | listed in the RFEF determination.\r\nFollowing this, we developed a | 71 | listed in the RFEF determination.\r\nFollowing this, we developed a | ||
72 | predictive statistical model of the probability of occurrence of RFEF | 72 | predictive statistical model of the probability of occurrence of RFEF | ||
73 | using plot data and a selection of environmental and remote-sensing | 73 | using plot data and a selection of environmental and remote-sensing | ||
74 | variables. For the north coast, we used a Random Forest model, while | 74 | variables. For the north coast, we used a Random Forest model, while | ||
75 | for the south coast we used a Boosted Regression Tree model.\r\nTo | 75 | for the south coast we used a Boosted Regression Tree model.\r\nTo | ||
76 | create the operational map, we assigned every mapped API polygon to | 76 | create the operational map, we assigned every mapped API polygon to | ||
77 | RFEF if appropriate based on the plot data, over-storey and | 77 | RFEF if appropriate based on the plot data, over-storey and | ||
78 | understorey attributes, landform features and modelled probabilities | 78 | understorey attributes, landform features and modelled probabilities | ||
79 | underlying each API polygon. \r\nWe mapped 3819 hectares of RFEF on | 79 | underlying each API polygon. \r\nWe mapped 3819 hectares of RFEF on | ||
80 | the south coast and 198 hectares of RFEF on the north | 80 | the south coast and 198 hectares of RFEF on the north | ||
81 | coast.\r\n\r\nOperational TEC Mapping have been derived by API at a | 81 | coast.\r\n\r\nOperational TEC Mapping have been derived by API at a | ||
82 | viewing scale between 1-4000 using ADS40 50 cm pixel imagery and 1 m | 82 | viewing scale between 1-4000 using ADS40 50 cm pixel imagery and 1 m | ||
83 | derived LIDAR DEM grids for floodplain EECs.", | 83 | derived LIDAR DEM grids for floodplain EECs.", | ||
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85 | "num_tags": 0, | 85 | "num_tags": 0, | ||
86 | "organization": { | 86 | "organization": { | ||
87 | "approval_status": "approved", | 87 | "approval_status": "approved", | ||
88 | "created": "2018-06-15T18:51:39.525982", | 88 | "created": "2018-06-15T18:51:39.525982", | ||
89 | "description": "EPA is the primary environmental regulator for New | 89 | "description": "EPA is the primary environmental regulator for New | ||
90 | South Wales. Its purpose is to improve environmental performance and | 90 | South Wales. Its purpose is to improve environmental performance and | ||
91 | waste management\r\n\r\nEPA works with the community, business, | 91 | waste management\r\n\r\nEPA works with the community, business, | ||
92 | industry and government to maintain a balance between protecting the | 92 | industry and government to maintain a balance between protecting the | ||
93 | environment, managing competing demands on the environment and | 93 | environment, managing competing demands on the environment and | ||
94 | supporting sustainable growth.\r\n\r\nEPA provides information and | 94 | supporting sustainable growth.\r\n\r\nEPA provides information and | ||
95 | guidance about a broad range of environmental issues and activities. | 95 | guidance about a broad range of environmental issues and activities. | ||
96 | It engages with the community and uses social research to inform | 96 | It engages with the community and uses social research to inform | ||
97 | priorities, policies and programs. It publishes scientific research | 97 | priorities, policies and programs. It publishes scientific research | ||
98 | and monitors trends in the state of the environment, and offers advice | 98 | and monitors trends in the state of the environment, and offers advice | ||
99 | and incentives to help business and industry improve their | 99 | and incentives to help business and industry improve their | ||
100 | environmental performance.\r\n\r\nSee: http://www.epa.nsw.gov.au\r\n", | 100 | environmental performance.\r\n\r\nSee: http://www.epa.nsw.gov.au\r\n", | ||
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107 | "title": "Environment Protection Authority (EPA)", | 107 | "title": "Environment Protection Authority (EPA)", | ||
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228 | "state": "active", | 228 | "state": "active", | ||
229 | "url": | 229 | "url": | ||
230 | ebmap.environment.nsw.gov.au/PlanningHtml5Viewer/?viewer=IFOA_Viewer", | 230 | ebmap.environment.nsw.gov.au/PlanningHtml5Viewer/?viewer=IFOA_Viewer", | ||
231 | "url_type": null | 231 | "url_type": null | ||
232 | } | 232 | } | ||
233 | ], | 233 | ], | ||
234 | "spatial": | 234 | "spatial": | ||
235 | [150.77762,-32.74726],[150.77762,-37.41703],[149.50438,-37.41703]]]}", | 235 | [150.77762,-32.74726],[150.77762,-37.41703],[149.50438,-37.41703]]]}", | ||
236 | "spatial_coverage": | 236 | "spatial_coverage": | ||
237 | [150.77762,-32.74726],[150.77762,-37.41703],[149.50438,-37.41703]]]}", | 237 | [150.77762,-32.74726],[150.77762,-37.41703],[149.50438,-37.41703]]]}", | ||
238 | "state": "active", | 238 | "state": "active", | ||
239 | "tags": [], | 239 | "tags": [], | ||
n | 240 | "temporal_coverage_from": "01/10/2016", | n | 240 | "temporal_coverage_from": "2016-10-01", |
241 | "temporal_coverage_to": "", | ||||
242 | "title": "Assessment of River-Flat Eucalypt forest on Coastal | 241 | "title": "Assessment of River-Flat Eucalypt forest on Coastal | ||
243 | floodplains TEC on NSW Crown Forest Estate", | 242 | floodplains TEC on NSW Crown Forest Estate", | ||
244 | "type": "dataset", | 243 | "type": "dataset", | ||
245 | "unpublished": "false", | 244 | "unpublished": "false", | ||
246 | "update_freq": "irregular", | 245 | "update_freq": "irregular", | ||
t | 247 | "url": "", | t | 246 | "url": null, |
248 | "version": null | 247 | "version": null | ||
249 | } | 248 | } |