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Added resource Modelling Areas of Habitat Significance for Vertebrate Fauna and Vascular Flora in NE NSW - CRA 1999 to Habitat Models for the Northern Comprehensive Regional Assessment (CRA) 1999
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Deleted resource Modelling Areas of Habitat Significance for Vertebrate Fauna and Vascular Flora in NE NSW - CRA 1999 from Habitat Models for the Northern Comprehensive Regional Assessment (CRA) 1999
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2 | "author_email": null, | 2 | "author_email": null, | ||
3 | "creator_user_id": "8d2ac61a-d63a-4456-a00d-b35fee4c4025", | 3 | "creator_user_id": "8d2ac61a-d63a-4456-a00d-b35fee4c4025", | ||
4 | "extras": [ | 4 | "extras": [ | ||
5 | { | 5 | { | ||
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", | ||
11 | "value": | 11 | "value": | ||
12 | at-models-for-the-northern-comprehensive-regional-assessment-cra-1999" | 12 | at-models-for-the-northern-comprehensive-regional-assessment-cra-1999" | ||
13 | } | 13 | } | ||
14 | ], | 14 | ], | ||
15 | "groups": [], | 15 | "groups": [], | ||
16 | "id": "db3b6443-da21-4502-adea-1dec2917bef8", | 16 | "id": "db3b6443-da21-4502-adea-1dec2917bef8", | ||
17 | "isopen": true, | 17 | "isopen": true, | ||
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", | ||
21 | "likes": 0, | 21 | "likes": 0, | ||
22 | "maintainer": null, | 22 | "maintainer": null, | ||
23 | "maintainer_email": null, | 23 | "maintainer_email": null, | ||
24 | "metadata_created": "2024-07-05T03:27:59.295071", | 24 | "metadata_created": "2024-07-05T03:27:59.295071", | ||
n | 25 | "metadata_modified": "2024-07-05T03:28:02.951491", | n | 25 | "metadata_modified": "2024-07-05T03:28:05.206472", |
26 | "name": | 26 | "name": | ||
27 | t-models-for-the-northern-comprehensive-regional-assessment-cra-1999", | 27 | t-models-for-the-northern-comprehensive-regional-assessment-cra-1999", | ||
28 | "notes": "This is a collection of 171 habitat quality models for | 28 | "notes": "This is a collection of 171 habitat quality models for | ||
29 | fauna species that were mapped across forest areas in the Upper North | 29 | fauna species that were mapped across forest areas in the Upper North | ||
30 | East (UNE) and the Lower North East (LNE) NSW during the Comprehensive | 30 | East (UNE) and the Lower North East (LNE) NSW during the Comprehensive | ||
31 | Regional Assessment (CRA) in 1999. They are 100m grids stored in MGA | 31 | Regional Assessment (CRA) in 1999. They are 100m grids stored in MGA | ||
32 | Zone 56 projection. 34 models are mapped on public tenure and 137 | 32 | Zone 56 projection. 34 models are mapped on public tenure and 137 | ||
33 | over all tenure. The \u2018public land\u2019 fauna models were those | 33 | over all tenure. The \u2018public land\u2019 fauna models were those | ||
34 | that modelled fairly on public land, some using Presence-Absence | 34 | that modelled fairly on public land, some using Presence-Absence | ||
35 | modelling, and were restricted to public land because the systematic | 35 | modelling, and were restricted to public land because the systematic | ||
36 | surveys were carried out there (eg. primarily NEFBS, State Forest EIS, | 36 | surveys were carried out there (eg. primarily NEFBS, State Forest EIS, | ||
37 | CRA). Some all-tenure (Presence-only) models were most likely have | 37 | CRA). Some all-tenure (Presence-only) models were most likely have | ||
38 | been cut to public land if it was considered that they modelled better | 38 | been cut to public land if it was considered that they modelled better | ||
39 | there. In this case there would be two versions of the same model, | 39 | there. In this case there would be two versions of the same model, | ||
40 | but only one was used in the CRA.\r\n\r\nIt was decided that the flora | 40 | but only one was used in the CRA.\r\n\r\nIt was decided that the flora | ||
41 | models would not be published due to their poor quality and their need | 41 | models would not be published due to their poor quality and their need | ||
42 | for updating with better records in the time since. \r\n\r\nNote that | 42 | for updating with better records in the time since. \r\n\r\nNote that | ||
43 | a revised edition of approximately a third of the models were produced | 43 | a revised edition of approximately a third of the models were produced | ||
44 | in 2008: | 44 | in 2008: | ||
45 | nsw.gov.au/dataset/revised-northern-cra-habitat-models-2008\r\n\r\nThe | 45 | nsw.gov.au/dataset/revised-northern-cra-habitat-models-2008\r\n\r\nThe | ||
46 | original models were produced as part of a Comprehensive Regional | 46 | original models were produced as part of a Comprehensive Regional | ||
47 | Assessment (CRA) for the Regional Forest Assessment (RFA) process. The | 47 | Assessment (CRA) for the Regional Forest Assessment (RFA) process. The | ||
48 | specific objective of these models was to _identify core areas of | 48 | specific objective of these models was to _identify core areas of | ||
49 | forest capable of sustaining viable populations of priority | 49 | forest capable of sustaining viable populations of priority | ||
50 | species_.\r\n\r\nHabitat quality models were derived using known | 50 | species_.\r\n\r\nHabitat quality models were derived using known | ||
51 | distributions of species combined with abiotic, biotic, terrain, | 51 | distributions of species combined with abiotic, biotic, terrain, | ||
52 | habitat and geographic layers within a GIS. These known | 52 | habitat and geographic layers within a GIS. These known | ||
53 | species-habitat relationships were then used to model predicted | 53 | species-habitat relationships were then used to model predicted | ||
54 | distributions and thus areas of significant habitat for the species of | 54 | distributions and thus areas of significant habitat for the species of | ||
55 | concern. Flora and fauna experts were used to validate the models and | 55 | concern. Flora and fauna experts were used to validate the models and | ||
56 | define areas of high-quality habitat for each species. The models are | 56 | define areas of high-quality habitat for each species. The models are | ||
57 | either mapped across All Tenure (at) or Public Tenure (pt). Each | 57 | either mapped across All Tenure (at) or Public Tenure (pt). Each | ||
58 | species model is named with the Catalogue of Australian Vertebrates | 58 | species model is named with the Catalogue of Australian Vertebrates | ||
59 | (CAVS) code. \r\n\r\n__Fauna models__ were developed using logistic | 59 | (CAVS) code. \r\n\r\n__Fauna models__ were developed using logistic | ||
60 | regression models (generalised additive models) of species presence | 60 | regression models (generalised additive models) of species presence | ||
61 | and absence to mapped environmental features. Where statistical models | 61 | and absence to mapped environmental features. Where statistical models | ||
62 | were judged by the expert panel to be inadequate, qualitative or | 62 | were judged by the expert panel to be inadequate, qualitative or | ||
63 | expert models were derived.\r\nAdditionally, fauna experts were used | 63 | expert models were derived.\r\nAdditionally, fauna experts were used | ||
64 | to identify habitat quality. Probability levels were used where | 64 | to identify habitat quality. Probability levels were used where | ||
65 | appropriate to define high (class 1), intermediate (class 2), and | 65 | appropriate to define high (class 1), intermediate (class 2), and | ||
66 | marginal (class 3) habitat. \r\n\r\n__Flora models__ were produced | 66 | marginal (class 3) habitat. \r\n\r\n__Flora models__ were produced | ||
67 | using a combination of GAM inference of species sightings with mapped | 67 | using a combination of GAM inference of species sightings with mapped | ||
68 | environmental features and a boolean overlay of selected environmental | 68 | environmental features and a boolean overlay of selected environmental | ||
69 | features along with expert review. Expert judgement was employed to | 69 | features along with expert review. Expert judgement was employed to | ||
70 | categorise flora habitat into two classes of potential habitat: | 70 | categorise flora habitat into two classes of potential habitat: | ||
71 | \r\nOccupied habitat (class 1) that shows validated point localities | 71 | \r\nOccupied habitat (class 1) that shows validated point localities | ||
72 | or population areas with a surrounding buffer to account for local | 72 | or population areas with a surrounding buffer to account for local | ||
73 | seed bank or regeneration.\r\nHigh quality habitat (class 2) which is | 73 | seed bank or regeneration.\r\nHigh quality habitat (class 2) which is | ||
74 | the rest of the model constructed using the boolean overlay of | 74 | the rest of the model constructed using the boolean overlay of | ||
75 | environmental layers.\r\n\r\nSee Table 3A (pg.33-38) in report for | 75 | environmental layers.\r\n\r\nSee Table 3A (pg.33-38) in report for | ||
76 | full a breakdown of species models, methods used and assessment of | 76 | full a breakdown of species models, methods used and assessment of | ||
77 | model confidence. \r\n\r\nThe report notes that models were not | 77 | model confidence. \r\n\r\nThe report notes that models were not | ||
78 | validated due to time constraints and that results should be viewed as | 78 | validated due to time constraints and that results should be viewed as | ||
79 | a \"minimum estimate of high-quality habitat for the purposes of the | 79 | a \"minimum estimate of high-quality habitat for the purposes of the | ||
80 | CRA.\" \r\n\r\nThe official report, _Modelling areas of habitat | 80 | CRA.\" \r\n\r\nThe official report, _Modelling areas of habitat | ||
81 | significance for vertebrate fauna and vascular flora in north-east NSW | 81 | significance for vertebrate fauna and vascular flora in north-east NSW | ||
82 | 1999_, expands on the methodology and outputs. The report is stored | 82 | 1999_, expands on the methodology and outputs. The report is stored | ||
83 | for internal access under | 83 | for internal access under | ||
84 | porate\\Products\\Biodiversity\\Habitat\\CRA_Northern\r\n\r\nMODELLING | 84 | porate\\Products\\Biodiversity\\Habitat\\CRA_Northern\r\n\r\nMODELLING | ||
85 | AREAS OF HABITAT SIGNIFICANCE FOR VERTEBRATE FAUNA AND VASCULAR FLORA | 85 | AREAS OF HABITAT SIGNIFICANCE FOR VERTEBRATE FAUNA AND VASCULAR FLORA | ||
86 | IN NORTH EAST NSW\r\nA project undertaken as part of the NSW | 86 | IN NORTH EAST NSW\r\nA project undertaken as part of the NSW | ||
87 | Comprehensive Regional Assessments, April 1999\r\nProject number NA | 87 | Comprehensive Regional Assessments, April 1999\r\nProject number NA | ||
88 | 23/EH\r\n\r\nThe fauna species modelled are as | 88 | 23/EH\r\n\r\nThe fauna species modelled are as | ||
89 | follows:\r\n\r\n\u2022\t0021\t Rose-crowned | 89 | follows:\r\n\r\n\u2022\t0021\t Rose-crowned | ||
90 | Fruit-Dove\r\n\u2022\t0023\t Superb Fruit-Dove\r\n\u2022\t0035\t Brush | 90 | Fruit-Dove\r\n\u2022\t0023\t Superb Fruit-Dove\r\n\u2022\t0035\t Brush | ||
91 | Bronzewing\r\n\u2022\t0174\t Bush Stone-curlew\r\n\u2022\t0183\t | 91 | Bronzewing\r\n\u2022\t0174\t Bush Stone-curlew\r\n\u2022\t0183\t | ||
92 | Black-necked Stork\r\n\u2022\t0196\t Black Bittern\r\n\u2022\t0223\t | 92 | Black-necked Stork\r\n\u2022\t0196\t Black Bittern\r\n\u2022\t0223\t | ||
93 | Red Goshawk\r\n\u2022\t0241\t Osprey\r\n\u2022\t0248\t Powerful | 93 | Red Goshawk\r\n\u2022\t0241\t Osprey\r\n\u2022\t0248\t Powerful | ||
94 | Owl\r\n\u2022\t0250\t Masked Owl\r\n\u2022\t0253\t Sooty | 94 | Owl\r\n\u2022\t0250\t Masked Owl\r\n\u2022\t0253\t Sooty | ||
95 | Owl\r\n\u2022\t0258\t Musk Lorikeet\r\n\u2022\t0264\t Red-tailed | 95 | Owl\r\n\u2022\t0258\t Musk Lorikeet\r\n\u2022\t0264\t Red-tailed | ||
96 | Black-Cockatoo\r\n\u2022\t0265\t Glossy | 96 | Black-Cockatoo\r\n\u2022\t0265\t Glossy | ||
97 | Black-Cockatoo\r\n\u2022\t0268\t Gang-gang Cockatoo\r\n\u2022\t0302\t | 97 | Black-Cockatoo\r\n\u2022\t0268\t Gang-gang Cockatoo\r\n\u2022\t0302\t | ||
98 | Turquoise Parrot\r\n\u2022\t0324\t Forest Kingfisher\r\n\u2022\t0345\t | 98 | Turquoise Parrot\r\n\u2022\t0324\t Forest Kingfisher\r\n\u2022\t0345\t | ||
99 | Little Bronze-Cuckoo\r\n\u2022\t0350\t Superb Lyrebird | 99 | Little Bronze-Cuckoo\r\n\u2022\t0350\t Superb Lyrebird | ||
100 | (edwardsii)\r\n\u2022\t0351\t Albert's Lyrebird\r\n\u2022\t0355\t | 100 | (edwardsii)\r\n\u2022\t0351\t Albert's Lyrebird\r\n\u2022\t0355\t | ||
101 | Rufous Scrub-bird\r\n\u2022\t0376\t White-eared | 101 | Rufous Scrub-bird\r\n\u2022\t0376\t White-eared | ||
102 | Monarch\r\n\u2022\t0385\t Hooded Robin\r\n\u2022\t0396\t Pale-yellow | 102 | Monarch\r\n\u2022\t0385\t Hooded Robin\r\n\u2022\t0396\t Pale-yellow | ||
103 | Robin\r\n\u2022\t0413\t Little Shrike-thrush\r\n\u2022\t0443\t | 103 | Robin\r\n\u2022\t0413\t Little Shrike-thrush\r\n\u2022\t0443\t | ||
104 | Grey-crowned Babbler\r\n\u2022\t0498\t Chestnut-rumped | 104 | Grey-crowned Babbler\r\n\u2022\t0498\t Chestnut-rumped | ||
105 | Hylacola\r\n\u2022\t0598\t Painted Honeyeater\r\n\u2022\t0603\t Regent | 105 | Hylacola\r\n\u2022\t0598\t Painted Honeyeater\r\n\u2022\t0603\t Regent | ||
106 | Honeyeater\r\n\u2022\t0610\t Mangrove Honeyeater\r\n\u2022\t0686\t | 106 | Honeyeater\r\n\u2022\t0610\t Mangrove Honeyeater\r\n\u2022\t0686\t | ||
107 | Paradise Riflebird\r\n\u2022\t0868\t Forest Raven\r\n\u2022\t1008\t | 107 | Paradise Riflebird\r\n\u2022\t0868\t Forest Raven\r\n\u2022\t1008\t | ||
108 | Tiger Quoll\r\n\u2022\t1017\t Brush-tailed | 108 | Tiger Quoll\r\n\u2022\t1017\t Brush-tailed | ||
109 | Phascogale\r\n\u2022\t1033\t Dusky Antechinus\r\n\u2022\t1045\t Common | 109 | Phascogale\r\n\u2022\t1033\t Dusky Antechinus\r\n\u2022\t1045\t Common | ||
110 | Planigale\r\n\u2022\t1136\t Yellow-bellied Glider\r\n\u2022\t1150\t | 110 | Planigale\r\n\u2022\t1136\t Yellow-bellied Glider\r\n\u2022\t1150\t | ||
111 | Eastern Pygmy-possum\r\n\u2022\t1162\t Koala\r\n\u2022\t1165\t Common | 111 | Eastern Pygmy-possum\r\n\u2022\t1162\t Koala\r\n\u2022\t1165\t Common | ||
112 | Wombat\r\n\u2022\t1175\t Long-nosed Potoroo\r\n\u2022\t1187\t Rufous | 112 | Wombat\r\n\u2022\t1175\t Long-nosed Potoroo\r\n\u2022\t1187\t Rufous | ||
113 | Bettong\r\n\u2022\t1215\t Brush-tailed Rock-wallaby\r\n\u2022\t1245\t | 113 | Bettong\r\n\u2022\t1215\t Brush-tailed Rock-wallaby\r\n\u2022\t1245\t | ||
114 | Parma Wallaby\r\n\u2022\t1259\t Whiptail Wallaby\r\n\u2022\t1280\t | 114 | Parma Wallaby\r\n\u2022\t1259\t Whiptail Wallaby\r\n\u2022\t1280\t | ||
115 | Pteropus poliocephalus\r\n\u2022\t1282\t Pteropus | 115 | Pteropus poliocephalus\r\n\u2022\t1282\t Pteropus | ||
116 | alecto\r\n\u2022\t1290\t Nyctimene robinsoni\r\n\u2022\t1294\t | 116 | alecto\r\n\u2022\t1290\t Nyctimene robinsoni\r\n\u2022\t1294\t | ||
117 | Syconycteris australis\r\n\u2022\t1303\t Rhinolophus | 117 | Syconycteris australis\r\n\u2022\t1303\t Rhinolophus | ||
118 | megaphyllus\r\n\u2022\t1324\t Nyctinomus australis\r\n\u2022\t1329\t | 118 | megaphyllus\r\n\u2022\t1324\t Nyctinomus australis\r\n\u2022\t1329\t | ||
119 | Mormopterus norfolkensis\r\n\u2022\t1336\t Nyctophilus | 119 | Mormopterus norfolkensis\r\n\u2022\t1336\t Nyctophilus | ||
120 | bifax\r\n\u2022\t1353\t Chalinolobus dwyeri\r\n\u2022\t1354\t | 120 | bifax\r\n\u2022\t1353\t Chalinolobus dwyeri\r\n\u2022\t1354\t | ||
121 | Chalinolobus nigrogriseus\r\n\u2022\t1361\t Scotoeanax | 121 | Chalinolobus nigrogriseus\r\n\u2022\t1361\t Scotoeanax | ||
122 | rueppellii\r\n\u2022\t1362\t Scotorepens greyii\r\n\u2022\t1364\t | 122 | rueppellii\r\n\u2022\t1362\t Scotorepens greyii\r\n\u2022\t1364\t | ||
123 | Scotorepens balstoni\r\n\u2022\t1369\t Kerivoula | 123 | Scotorepens balstoni\r\n\u2022\t1369\t Kerivoula | ||
124 | papuensis\r\n\u2022\t1372\t Falsistrellus | 124 | papuensis\r\n\u2022\t1372\t Falsistrellus | ||
125 | tasmaniensis\r\n\u2022\t1377\t Vespadelus pumilus\r\n\u2022\t1401\t | 125 | tasmaniensis\r\n\u2022\t1377\t Vespadelus pumilus\r\n\u2022\t1401\t | ||
126 | Pale Field-rat\r\n\u2022\t1455\t New Holland Mouse\r\n\u2022\t1466\t | 126 | Pale Field-rat\r\n\u2022\t1455\t New Holland Mouse\r\n\u2022\t1466\t | ||
127 | Eastern Chestnut Mouse\r\n\u2022\t2124\t Eulamprus | 127 | Eastern Chestnut Mouse\r\n\u2022\t2124\t Eulamprus | ||
128 | tryoni\r\n\u2022\t2139\t Underwoodisaurus sphyrurus\r\n\u2022\t2182\t | 128 | tryoni\r\n\u2022\t2139\t Underwoodisaurus sphyrurus\r\n\u2022\t2182\t | ||
129 | Tympanocryptis diemensis\r\n\u2022\t2245\t Hypsilurus | 129 | Tympanocryptis diemensis\r\n\u2022\t2245\t Hypsilurus | ||
130 | spinipes\r\n\u2022\t2287\t Varanus rosenbergi\r\n\u2022\t2294\t | 130 | spinipes\r\n\u2022\t2287\t Varanus rosenbergi\r\n\u2022\t2294\t | ||
131 | Ophioscincus truncatus\r\n\u2022\t2453\t Lampropholis | 131 | Ophioscincus truncatus\r\n\u2022\t2453\t Lampropholis | ||
132 | caligula\r\n\u2022\t2467\t Cautula zia\r\n\u2022\t2468\t Ctenotus | 132 | caligula\r\n\u2022\t2467\t Cautula zia\r\n\u2022\t2468\t Ctenotus | ||
133 | eurydice\r\n\u2022\t2550\t Eulamprus kosciuskoi\r\n\u2022\t2559\t | 133 | eurydice\r\n\u2022\t2550\t Eulamprus kosciuskoi\r\n\u2022\t2559\t | ||
134 | Eulamprus tenuis\r\n\u2022\t2615\t Austrelaps | 134 | Eulamprus tenuis\r\n\u2022\t2615\t Austrelaps | ||
135 | ramsayi\r\n\u2022\t2645\t Cacophis harriettae\r\n\u2022\t2665\t | 135 | ramsayi\r\n\u2022\t2645\t Cacophis harriettae\r\n\u2022\t2665\t | ||
136 | Drysdalia coronoides\r\n\u2022\t2675\t Hoplocephalus | 136 | Drysdalia coronoides\r\n\u2022\t2675\t Hoplocephalus | ||
137 | bitorquatus\r\n\u2022\t2676\t Hoplocephalus | 137 | bitorquatus\r\n\u2022\t2676\t Hoplocephalus | ||
138 | bungaroides\r\n\u2022\t2687\t Saltuarius swaini\r\n\u2022\t3007\t Assa | 138 | bungaroides\r\n\u2022\t2687\t Saltuarius swaini\r\n\u2022\t3007\t Assa | ||
139 | darlingtoni\r\n\u2022\t3008\t Mixophyes fleayi\r\n\u2022\t3039\t | 139 | darlingtoni\r\n\u2022\t3008\t Mixophyes fleayi\r\n\u2022\t3039\t | ||
140 | Litoria littlejohni\r\n\u2022\t3042\t Heleioporus | 140 | Litoria littlejohni\r\n\u2022\t3042\t Heleioporus | ||
141 | australiacus\r\n\u2022\t3073\t Mixophyes balbus\r\n\u2022\t3075\t | 141 | australiacus\r\n\u2022\t3073\t Mixophyes balbus\r\n\u2022\t3075\t | ||
142 | Mixophyes iteratus\r\n\u2022\t3107\t Philoria | 142 | Mixophyes iteratus\r\n\u2022\t3107\t Philoria | ||
143 | kundagungan\r\n\u2022\t3109\t Philoria sphagnicolus\r\n\u2022\t3117\t | 143 | kundagungan\r\n\u2022\t3109\t Philoria sphagnicolus\r\n\u2022\t3117\t | ||
144 | Pseudophryne bibronii\r\n\u2022\t3166\t Litoria | 144 | Pseudophryne bibronii\r\n\u2022\t3166\t Litoria | ||
145 | aurea\r\n\u2022\t3168\t Litoria booroolongensis\r\n\u2022\t3169\t | 145 | aurea\r\n\u2022\t3168\t Litoria booroolongensis\r\n\u2022\t3169\t | ||
146 | Litoria brevipalmata\r\n\u2022\t3186\t Litoria | 146 | Litoria brevipalmata\r\n\u2022\t3186\t Litoria | ||
147 | subglandulosa\r\n\u2022\t3202\t Litoria | 147 | subglandulosa\r\n\u2022\t3202\t Litoria | ||
148 | olongburensis\r\n\u2022\t3217\t Litoria piperata\r\n\u2022\t3219\t | 148 | olongburensis\r\n\u2022\t3217\t Litoria piperata\r\n\u2022\t3219\t | ||
149 | Litoria revelata\r\n\u2022\t9004\t Saproscincus | 149 | Litoria revelata\r\n\u2022\t9004\t Saproscincus | ||
150 | challengeri\r\n\u2022\t9006\t Philoria pughi\r\n\u2022\t9007\t | 150 | challengeri\r\n\u2022\t9006\t Philoria pughi\r\n\u2022\t9007\t | ||
151 | Philoria richmondensis\r\n\u2022\t9029\t Scotorepens sp | 151 | Philoria richmondensis\r\n\u2022\t9029\t Scotorepens sp | ||
152 | 1\r\n\u2022\t9058\t Lampropholis elongata\r\n\u2022\t9059\t Elseya | 152 | 1\r\n\u2022\t9058\t Lampropholis elongata\r\n\u2022\t9059\t Elseya | ||
153 | georgesi\r\n\u2022\t9060\t Elseya purvisi\r\n\u2022\t9061\t Emydura sp | 153 | georgesi\r\n\u2022\t9060\t Elseya purvisi\r\n\u2022\t9061\t Emydura sp | ||
154 | 1\r\n\u2022\t9103\t Elseya sp 2\r\n\u2022\t0017\t Black-breasted | 154 | 1\r\n\u2022\t9103\t Elseya sp 2\r\n\u2022\t0017\t Black-breasted | ||
155 | Button-quail\r\n\u2022\t0025\t Wompoo Fruit-Dove\r\n\u2022\t0230\t | 155 | Button-quail\r\n\u2022\t0025\t Wompoo Fruit-Dove\r\n\u2022\t0230\t | ||
156 | Square-tailed Kite\r\n\u2022\t0234\t Pacific Baza\r\n\u2022\t0246\t | 156 | Square-tailed Kite\r\n\u2022\t0234\t Pacific Baza\r\n\u2022\t0246\t | ||
157 | Barking Owl\r\n\u2022\t0261\t Double-eyed Fig-Parrot\r\n\u2022\t0309\t | 157 | Barking Owl\r\n\u2022\t0261\t Double-eyed Fig-Parrot\r\n\u2022\t0309\t | ||
158 | Swift Parrot\r\n\u2022\t0314\t Marbled Frogmouth\r\n\u2022\t0405\t | 158 | Swift Parrot\r\n\u2022\t0314\t Marbled Frogmouth\r\n\u2022\t0405\t | ||
159 | Olive Whistler\r\n\u2022\t0428\t Barred | 159 | Olive Whistler\r\n\u2022\t0428\t Barred | ||
160 | Cuckoo-shrike\r\n\u2022\t0519\t Eastern Bristlebird\r\n\u2022\t0619\t | 160 | Cuckoo-shrike\r\n\u2022\t0519\t Eastern Bristlebird\r\n\u2022\t0619\t | ||
161 | Yellow-tufted Honeyeater\r\n\u2022\t1025\t Vespadelus | 161 | Yellow-tufted Honeyeater\r\n\u2022\t1025\t Vespadelus | ||
162 | troughtoni\r\n\u2022\t1133\t Greater Glider\r\n\u2022\t1137\t Squirrel | 162 | troughtoni\r\n\u2022\t1133\t Greater Glider\r\n\u2022\t1137\t Squirrel | ||
163 | Glider\r\n\u2022\t1234\t Red-legged Pademelon\r\n\u2022\t1260\t | 163 | Glider\r\n\u2022\t1234\t Red-legged Pademelon\r\n\u2022\t1260\t | ||
164 | Black-striped Wallaby\r\n\u2022\t1341\t Miniopterus | 164 | Black-striped Wallaby\r\n\u2022\t1341\t Miniopterus | ||
165 | schreibersii\r\n\u2022\t1346\t Miniopterus australis\r\n\u2022\t1357\t | 165 | schreibersii\r\n\u2022\t1346\t Miniopterus australis\r\n\u2022\t1357\t | ||
166 | Myotis adversus\r\n\u2022\t1438\t Broad-toothed Rat\r\n\u2022\t1464\t | 166 | Myotis adversus\r\n\u2022\t1438\t Broad-toothed Rat\r\n\u2022\t1464\t | ||
167 | Hastings River Mouse\r\n\u2022\t1500\t Grassland | 167 | Hastings River Mouse\r\n\u2022\t1500\t Grassland | ||
168 | Melomys\r\n\u2022\t1531\t Dingo\r\n\u2022\t2293\t Coeranoscincus | 168 | Melomys\r\n\u2022\t1531\t Dingo\r\n\u2022\t2293\t Coeranoscincus | ||
169 | reticulatus\r\n\u2022\t2552\t Eulamprus murrayi\r\n\u2022\t2640\t | 169 | reticulatus\r\n\u2022\t2552\t Eulamprus murrayi\r\n\u2022\t2640\t | ||
170 | Acanthophis antarcticus\r\n\u2022\t2677\t Hoplocephalus | 170 | Acanthophis antarcticus\r\n\u2022\t2677\t Hoplocephalus | ||
171 | stephensii\r\n\u2022\t2723\t Tropidechis carinatus\r\n\u2022\t2764\t | 171 | stephensii\r\n\u2022\t2723\t Tropidechis carinatus\r\n\u2022\t2764\t | ||
172 | Saproscincus galli\r\n\u2022\t2765\t Saproscincus | 172 | Saproscincus galli\r\n\u2022\t2765\t Saproscincus | ||
173 | rosei\r\n\u2022\t3108\t Philoria loveridgei\r\n\u2022\t3137\t Crinia | 173 | rosei\r\n\u2022\t3108\t Philoria loveridgei\r\n\u2022\t3137\t Crinia | ||
174 | tinnula\r\n\u2022\t3184\t Litoria freycineti\r\n\u2022\t3190\t Litoria | 174 | tinnula\r\n\u2022\t3184\t Litoria freycineti\r\n\u2022\t3190\t Litoria | ||
175 | jervisiensis\r\n", | 175 | jervisiensis\r\n", | ||
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278 | "state": "active", | 278 | "state": "active", | ||
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280 | { | 280 | { | ||
281 | "display_name": "Fauna", | 281 | "display_name": "Fauna", | ||
282 | "id": "eced8f87-5ac6-4a0a-8f05-6211c23cf31f", | 282 | "id": "eced8f87-5ac6-4a0a-8f05-6211c23cf31f", | ||
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296 | "id": "7fa2db19-53db-4d39-a4cf-cb8935ba90ee", | 296 | "id": "7fa2db19-53db-4d39-a4cf-cb8935ba90ee", | ||
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299 | "vocabulary_id": null | 299 | "vocabulary_id": null | ||
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303 | "id": "5a33b55e-c7aa-4d47-ae82-22afaf874c64", | 303 | "id": "5a33b55e-c7aa-4d47-ae82-22afaf874c64", | ||
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306 | "vocabulary_id": null | 306 | "vocabulary_id": null | ||
307 | } | 307 | } | ||
308 | ], | 308 | ], | ||
309 | "temporal_coverage_from": "1999-04-01", | 309 | "temporal_coverage_from": "1999-04-01", | ||
310 | "temporal_coverage_to": "1999-04-02", | 310 | "temporal_coverage_to": "1999-04-02", | ||
311 | "title": "Habitat Models for the Northern Comprehensive Regional | 311 | "title": "Habitat Models for the Northern Comprehensive Regional | ||
312 | Assessment (CRA) 1999", | 312 | Assessment (CRA) 1999", | ||
313 | "type": "dataset", | 313 | "type": "dataset", | ||
314 | "unpublished": "false", | 314 | "unpublished": "false", | ||
315 | "update_freq": "notPlanned", | 315 | "update_freq": "notPlanned", | ||
316 | "url": null, | 316 | "url": null, | ||
317 | "version": null | 317 | "version": null | ||
318 | } | 318 | } |