Changes
On March 14, 2024 at 1:02:31 AM +1100, National Native Title Tribunal:
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Added resource Native Forestry Map Viewer to Assessment of Rainforest TECS 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 Rainforest TECS on NSW Crown Forest Estate
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Added resource Operational Map for Lowland Rainforest on Floodplain Threatened Ecological Community on NSW Crown Forest Estate to Assessment of Rainforest TECS on NSW Crown Forest Estate
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Added resource Operational Map for Lowland Rainforest Threatened Ecological Community on NSW Crown Forest Estate to Assessment of Rainforest TECS on NSW Crown Forest Estate
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Added resource Data Quality Statement to Assessment of Rainforest TECS on NSW Crown Forest Estate
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Added resource Assessment of Rainforest TECS on NSW Crown Forest Estate to Assessment of Rainforest TECS on NSW Crown Forest Estate
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Deleted resource Assessment of Rainforest TECS on NSW Crown Forest Estate from Assessment of Rainforest TECS on NSW Crown Forest Estate
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Deleted resource Native Forestry Map Viewer from Assessment of Rainforest TECS 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 Rainforest TECS on NSW Crown Forest Estate
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Deleted resource Data Quality Statement from Assessment of Rainforest TECS on NSW Crown Forest Estate
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Deleted resource Operational Map for Lowland Rainforest Threatened Ecological Community on NSW Crown Forest Estate from Assessment of Rainforest TECS on NSW Crown Forest Estate
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Deleted resource Operational Map for Lowland Rainforest on Floodplain Threatened Ecological Community on NSW Crown Forest Estate from Assessment of Rainforest TECS on NSW Crown Forest Estate
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7 | "value": "SEED" | 7 | "value": "SEED" | ||
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10 | "key": "harvest_url", | 10 | "key": "harvest_url", | ||
11 | "value": | 11 | "value": | ||
12 | d.nsw.gov.au/dataset/assessment-of-rainforest-tecs-of-the-north-coast" | 12 | d.nsw.gov.au/dataset/assessment-of-rainforest-tecs-of-the-north-coast" | ||
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18 | "license_id": "cc-by", | 18 | "license_id": "cc-by", | ||
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": "2018-06-15T08:52:46.880282", | 24 | "metadata_created": "2018-06-15T08:52:46.880282", | ||
n | 25 | "metadata_modified": "2024-03-13T09:52:21.555770", | n | 25 | "metadata_modified": "2024-03-13T14:02:31.471619", |
26 | "name": "assessment-of-rainforest-tecs-of-the-north-coast", | 26 | "name": "assessment-of-rainforest-tecs-of-the-north-coast", | ||
27 | "notes": "Operational map for Lowland Rainforest:\r\n\r\nThe | 27 | "notes": "Operational map for Lowland Rainforest:\r\n\r\nThe | ||
28 | operational map for Lowland Rainforest (LORF) was constructed to | 28 | operational map for Lowland Rainforest (LORF) was constructed to | ||
29 | resolve long-standing issues surrounding its identification, location | 29 | resolve long-standing issues surrounding its identification, location | ||
30 | and extent within the NSW State Forest estate covered by the coastal | 30 | and extent within the NSW State Forest estate covered by the coastal | ||
31 | Integrated Forestry Operation Agreements. \r\nThe project\u2019s | 31 | Integrated Forestry Operation Agreements. \r\nThe project\u2019s | ||
32 | Threatened Ecological Community (TEC) Reference Panel (the Panel) | 32 | Threatened Ecological Community (TEC) Reference Panel (the Panel) | ||
33 | preceded the assessment process by reviewing the determination for | 33 | preceded the assessment process by reviewing the determination for | ||
34 | LORF. The Panel found that the determination for LORF relies almost | 34 | LORF. The Panel found that the determination for LORF relies almost | ||
35 | exclusively on a rainforest classification system described by Floyd | 35 | exclusively on a rainforest classification system described by Floyd | ||
36 | (1990) where several rainforest \u2018suballiances\u2019 make up the | 36 | (1990) where several rainforest \u2018suballiances\u2019 make up the | ||
37 | LORF assemblage. Floyd\u2019s suballiance classifications presented a | 37 | LORF assemblage. Floyd\u2019s suballiance classifications presented a | ||
38 | challenge to our project as they were largely subjective and were not | 38 | challenge to our project as they were largely subjective and were not | ||
39 | compatible with quantitative analysis, meaning that it was difficult | 39 | compatible with quantitative analysis, meaning that it was difficult | ||
40 | to distinguish between the LORF TEC and other rainforest vegetation | 40 | to distinguish between the LORF TEC and other rainforest vegetation | ||
41 | using statistically sound methods. \r\nTo overcome some of these | 41 | using statistically sound methods. \r\nTo overcome some of these | ||
42 | problems we revisited a set of reference sites that were assigned by | 42 | problems we revisited a set of reference sites that were assigned by | ||
43 | Floyd to the suballiances cited in the LORF determination and in other | 43 | Floyd to the suballiances cited in the LORF determination and in other | ||
44 | rainforest TEC determinations, and collected new floristic data using | 44 | rainforest TEC determinations, and collected new floristic data using | ||
45 | standard flora survey methods. We also targeted a range of localities | 45 | standard flora survey methods. We also targeted a range of localities | ||
46 | on State Forest that we considered likely to include LORF and other | 46 | on State Forest that we considered likely to include LORF and other | ||
47 | rainforest TECs based on the suballiance descriptions, cited | 47 | rainforest TECs based on the suballiance descriptions, cited | ||
48 | localities in Floyd (1990), and preliminary distribution models. Over | 48 | localities in Floyd (1990), and preliminary distribution models. Over | ||
49 | 300 new rainforest plots were combined with a large pool of existing | 49 | 300 new rainforest plots were combined with a large pool of existing | ||
50 | data covering eastern NSW to construct a provisional revised | 50 | data covering eastern NSW to construct a provisional revised | ||
51 | rainforest classification. We used the rainforest groups derived from | 51 | rainforest classification. We used the rainforest groups derived from | ||
52 | this analysis to compare the species composition of Floyd\u2019s | 52 | this analysis to compare the species composition of Floyd\u2019s | ||
53 | suballiances, determination assemblage lists and recent rainforest | 53 | suballiances, determination assemblage lists and recent rainforest | ||
54 | classifications included in regional classifications. Rainforest | 54 | classifications included in regional classifications. Rainforest | ||
55 | groups (and the plots that defined them) were assigned to the Floyd | 55 | groups (and the plots that defined them) were assigned to the Floyd | ||
56 | suballiance with the highest degree of floristic similarity. We | 56 | suballiance with the highest degree of floristic similarity. We | ||
57 | conferred with the Panel to resolve any inconsistencies between the | 57 | conferred with the Panel to resolve any inconsistencies between the | ||
58 | results of our analyses and statements relating to the distribution | 58 | results of our analyses and statements relating to the distribution | ||
59 | and composition of individual suballiances in Floyd (1990) and the | 59 | and composition of individual suballiances in Floyd (1990) and the | ||
60 | determinations.\r\nWe then used plot data and a selection of | 60 | determinations.\r\nWe then used plot data and a selection of | ||
61 | environmental and remote-sensing variables to develop a Random Forest | 61 | environmental and remote-sensing variables to develop a Random Forest | ||
62 | (RF) model of the probability of occurrence of LORF. We assessed the | 62 | (RF) model of the probability of occurrence of LORF. We assessed the | ||
63 | location of plots assigned to LORF against the distribution of the RF | 63 | location of plots assigned to LORF against the distribution of the RF | ||
64 | model on and adjoining State Forests. We then completed detailed | 64 | model on and adjoining State Forests. We then completed detailed | ||
65 | aerial photograph interpretation (API) using a prescribed set of | 65 | aerial photograph interpretation (API) using a prescribed set of | ||
66 | mapping classes to delineate rainforest areas for a range of canopy | 66 | mapping classes to delineate rainforest areas for a range of canopy | ||
67 | cover thresholds. We constructed an operational map of LORF by | 67 | cover thresholds. We constructed an operational map of LORF by | ||
68 | assigning our API polygons as being LORF based on the modelled | 68 | assigning our API polygons as being LORF based on the modelled | ||
69 | probabilities and plot data underlying the polygon.\r\nOur mapping | 69 | probabilities and plot data underlying the polygon.\r\nOur mapping | ||
70 | identified a total of approximately 14,036 hectares of LORF, the vast | 70 | identified a total of approximately 14,036 hectares of LORF, the vast | ||
71 | majority of which was located in the north coast region. We mapped | 71 | majority of which was located in the north coast region. We mapped | ||
72 | 13,209 hectares of LORF on the north coast, with the largest areas | 72 | 13,209 hectares of LORF on the north coast, with the largest areas | ||
73 | found in Ewingar and Unumgar State Forests. Only 827 hectares of LORF | 73 | found in Ewingar and Unumgar State Forests. Only 827 hectares of LORF | ||
74 | were mapped on the south coast, with the largest areas found in | 74 | were mapped on the south coast, with the largest areas found in | ||
75 | Yadboro and Currowan State Forests.\r\n\r\nOperational map for Lowland | 75 | Yadboro and Currowan State Forests.\r\n\r\nOperational map for Lowland | ||
76 | Rainforest on Floodplains:\r\n\r\nThe operational map for Lowland | 76 | Rainforest on Floodplains:\r\n\r\nThe operational map for Lowland | ||
77 | Rainforest on Floodplains (LRFP) was constructed to resolve | 77 | Rainforest on Floodplains (LRFP) was constructed to resolve | ||
78 | long-standing issues surrounding its identification, location and | 78 | long-standing issues surrounding its identification, location and | ||
79 | extent within the NSW State Forest estate covered by the coastal | 79 | extent within the NSW State Forest estate covered by the coastal | ||
80 | Integrated Forestry Operation Agreements. \r\nThe project\u2019s | 80 | Integrated Forestry Operation Agreements. \r\nThe project\u2019s | ||
81 | Threatened Ecological Community (TEC) Reference Panel (the Panel) | 81 | Threatened Ecological Community (TEC) Reference Panel (the Panel) | ||
82 | preceded the assessment process by reviewing the determination for | 82 | preceded the assessment process by reviewing the determination for | ||
83 | LRFP. The Panel found that the determination for LRFP relies mainly | 83 | LRFP. The Panel found that the determination for LRFP relies mainly | ||
84 | on a rainforest classification system described by Floyd (1990) where | 84 | on a rainforest classification system described by Floyd (1990) where | ||
85 | several rainforest \u2018suballiances\u2019 make up the LRFP | 85 | several rainforest \u2018suballiances\u2019 make up the LRFP | ||
86 | assemblage. The determination also identifies a range of floodplain | 86 | assemblage. The determination also identifies a range of floodplain | ||
87 | and alluvial descriptors. Floyd\u2019s suballiance classifications | 87 | and alluvial descriptors. Floyd\u2019s suballiance classifications | ||
88 | presented a challenge to our project as they were largely subjective | 88 | presented a challenge to our project as they were largely subjective | ||
89 | and were not compatible with quantitative analysis, meaning that it | 89 | and were not compatible with quantitative analysis, meaning that it | ||
90 | was difficult to distinguish between the LRFP TEC and other rainforest | 90 | was difficult to distinguish between the LRFP TEC and other rainforest | ||
91 | vegetation using statistically sound methods. \r\nTo overcome some of | 91 | vegetation using statistically sound methods. \r\nTo overcome some of | ||
92 | these problems we revisited a set of reference sites that were | 92 | these problems we revisited a set of reference sites that were | ||
93 | assigned by Floyd to the suballiances cited in the LRFP determination | 93 | assigned by Floyd to the suballiances cited in the LRFP determination | ||
94 | and other rainforest TEC determinations, and collected new floristic | 94 | and other rainforest TEC determinations, and collected new floristic | ||
95 | data using standard flora survey methods. We also targeted a range of | 95 | data using standard flora survey methods. We also targeted a range of | ||
96 | localities on State Forest that we considered likely to include LRFP | 96 | localities on State Forest that we considered likely to include LRFP | ||
97 | and other rainforest TECs based on the suballiance descriptions, cited | 97 | and other rainforest TECs based on the suballiance descriptions, cited | ||
98 | localities in Floyd (1990), and preliminary distribution models. Over | 98 | localities in Floyd (1990), and preliminary distribution models. Over | ||
99 | 300 new rainforest plots were combined with a large pool of existing | 99 | 300 new rainforest plots were combined with a large pool of existing | ||
100 | data covering eastern NSW to construct a provisional revised | 100 | data covering eastern NSW to construct a provisional revised | ||
101 | rainforest classification. We used the rainforest groups derived from | 101 | rainforest classification. We used the rainforest groups derived from | ||
102 | this analysis to compare the species composition of Floyd | 102 | this analysis to compare the species composition of Floyd | ||
103 | suballiances, determination assemblage lists and recent rainforest | 103 | suballiances, determination assemblage lists and recent rainforest | ||
104 | classifications included in regional classifications. Rainforest | 104 | classifications included in regional classifications. Rainforest | ||
105 | groups, (and the plots that defined them), were assigned to the Floyd | 105 | groups, (and the plots that defined them), were assigned to the Floyd | ||
106 | suballiance with the highest degree of floristic similarity. We | 106 | suballiance with the highest degree of floristic similarity. We | ||
107 | conferred with the TEC Project Reference Panel (the Panel) to resolve | 107 | conferred with the TEC Project Reference Panel (the Panel) to resolve | ||
108 | inconsistencies between the results of our analyses and statements | 108 | inconsistencies between the results of our analyses and statements | ||
109 | relating to the distribution and composition of individual | 109 | relating to the distribution and composition of individual | ||
110 | suballiances in Floyd (1990), and the determinations.\r\nWe attempted | 110 | suballiances in Floyd (1990), and the determinations.\r\nWe attempted | ||
111 | to use plot data and a selection of environmental and remote-sensing | 111 | to use plot data and a selection of environmental and remote-sensing | ||
112 | variable to develop Random Forest models of the probability of | 112 | variable to develop Random Forest models of the probability of | ||
113 | occurrence of LRFP, but we were unable to assign any of our rainforest | 113 | occurrence of LRFP, but we were unable to assign any of our rainforest | ||
114 | groups to the assemblage lists or the primary suballiances cited in | 114 | groups to the assemblage lists or the primary suballiances cited in | ||
115 | the LRFP determination. We overcame this problem by constructing a | 115 | the LRFP determination. We overcame this problem by constructing a | ||
116 | fine scale digital elevation model (DEM) of landscape elements that we | 116 | fine scale digital elevation model (DEM) of landscape elements that we | ||
117 | considered were likely to be associated with the range of floodplain | 117 | considered were likely to be associated with the range of floodplain | ||
118 | and alluvial descriptors identified in the determination for LRFP. We | 118 | and alluvial descriptors identified in the determination for LRFP. We | ||
119 | then mapped our rainforest groups onto the DEM and assigned any | 119 | then mapped our rainforest groups onto the DEM and assigned any | ||
120 | rainforest assemblage that overlapped with our alluvial and floodplain | 120 | rainforest assemblage that overlapped with our alluvial and floodplain | ||
121 | DEM map as LRFP TEC. Using this method we constructed an operational | 121 | DEM map as LRFP TEC. Using this method we constructed an operational | ||
122 | map of LRFP in State Forests on the NSW coast. Our mapped identified a | 122 | map of LRFP in State Forests on the NSW coast. Our mapped identified a | ||
123 | total of 680 hectares of LRFP, all of which was located in the north | 123 | total of 680 hectares of LRFP, all of which was located in the north | ||
124 | coast region. \r\n\r\nOperational TEC Mapping have been derived by API | 124 | coast region. \r\n\r\nOperational TEC Mapping have been derived by API | ||
125 | at a viewing scale between 1-4000 using ADS40 50 cm pixel imagery and | 125 | at a viewing scale between 1-4000 using ADS40 50 cm pixel imagery and | ||
126 | 1 m derived LIDAR DEM grids for floodplain EECs.", | 126 | 1 m derived LIDAR DEM grids for floodplain EECs.", | ||
127 | "num_resources": 6, | 127 | "num_resources": 6, | ||
128 | "num_tags": 0, | 128 | "num_tags": 0, | ||
129 | "organization": { | 129 | "organization": { | ||
130 | "approval_status": "approved", | 130 | "approval_status": "approved", | ||
131 | "created": "2018-06-15T18:51:39.525982", | 131 | "created": "2018-06-15T18:51:39.525982", | ||
132 | "description": "EPA is the primary environmental regulator for New | 132 | "description": "EPA is the primary environmental regulator for New | ||
133 | South Wales. Its purpose is to improve environmental performance and | 133 | South Wales. Its purpose is to improve environmental performance and | ||
134 | waste management\r\n\r\nEPA works with the community, business, | 134 | waste management\r\n\r\nEPA works with the community, business, | ||
135 | industry and government to maintain a balance between protecting the | 135 | industry and government to maintain a balance between protecting the | ||
136 | environment, managing competing demands on the environment and | 136 | environment, managing competing demands on the environment and | ||
137 | supporting sustainable growth.\r\n\r\nEPA provides information and | 137 | supporting sustainable growth.\r\n\r\nEPA provides information and | ||
138 | guidance about a broad range of environmental issues and activities. | 138 | guidance about a broad range of environmental issues and activities. | ||
139 | It engages with the community and uses social research to inform | 139 | It engages with the community and uses social research to inform | ||
140 | priorities, policies and programs. It publishes scientific research | 140 | priorities, policies and programs. It publishes scientific research | ||
141 | and monitors trends in the state of the environment, and offers advice | 141 | and monitors trends in the state of the environment, and offers advice | ||
142 | and incentives to help business and industry improve their | 142 | and incentives to help business and industry improve their | ||
143 | environmental performance.\r\n\r\nSee: http://www.epa.nsw.gov.au\r\n", | 143 | environmental performance.\r\n\r\nSee: http://www.epa.nsw.gov.au\r\n", | ||
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149 | "state": "active", | 149 | "state": "active", | ||
150 | "title": "Environment Protection Authority (EPA)", | 150 | "title": "Environment Protection Authority (EPA)", | ||
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152 | }, | 152 | }, | ||
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