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f | 1 | { | f | 1 | { |
2 | "additional_informations": "", | 2 | "additional_informations": "", | ||
3 | "author": null, | 3 | "author": null, | ||
4 | "author_email": null, | 4 | "author_email": null, | ||
5 | "autonotes": "", | 5 | "autonotes": "", | ||
6 | "category": "types_of_habitat", | 6 | "category": "types_of_habitat", | ||
7 | "child_of_string": "", | 7 | "child_of_string": "", | ||
8 | "children": "", | 8 | "children": "", | ||
n | n | 9 | "clusters": [], | ||
9 | "coastal-land-use-and-planning": [ | 10 | "coastal-land-use-and-planning": [ | ||
10 | "planning-strategic-national-eu-regulated", | 11 | "planning-strategic-national-eu-regulated", | ||
11 | "planning-strategic-national-others", | 12 | "planning-strategic-national-others", | ||
12 | "planning-strategic-subnational", | 13 | "planning-strategic-subnational", | ||
13 | "planning-strategic-local", | 14 | "planning-strategic-local", | ||
14 | "planning-coordination-sub-national", | 15 | "planning-coordination-sub-national", | ||
15 | "planning-operational-sub-national" | 16 | "planning-operational-sub-national" | ||
16 | ], | 17 | ], | ||
17 | "conservation-types": [], | 18 | "conservation-types": [], | ||
18 | "creator_user_id": "c1526409-0a5f-4f99-9221-d0b97cff0942", | 19 | "creator_user_id": "c1526409-0a5f-4f99-9221-d0b97cff0942", | ||
19 | "crs": [ | 20 | "crs": [ | ||
20 | "other" | 21 | "other" | ||
21 | ], | 22 | ], | ||
22 | "crs_other": "", | 23 | "crs_other": "", | ||
23 | "data_accessibility": "Data available on request. Article still not | 24 | "data_accessibility": "Data available on request. Article still not | ||
24 | published so avoid external sharing. contact mfianchini@ogs.it", | 25 | published so avoid external sharing. contact mfianchini@ogs.it", | ||
25 | "data_portal": "", | 26 | "data_portal": "", | ||
26 | "derived": "", | 27 | "derived": "", | ||
27 | "derives_from_string": "", | 28 | "derives_from_string": "", | ||
28 | "domain_area": "mediterranean_sea", | 29 | "domain_area": "mediterranean_sea", | ||
29 | "ecosystem-services": [], | 30 | "ecosystem-services": [], | ||
30 | "environment-msfd-classes": [ | 31 | "environment-msfd-classes": [ | ||
31 | "habitats-seabed", | 32 | "habitats-seabed", | ||
32 | "pressure-biological-input-or-spread-of-non-indigenous-species" | 33 | "pressure-biological-input-or-spread-of-non-indigenous-species" | ||
33 | ], | 34 | ], | ||
34 | "environment-msfd-descriptors-criteria": [ | 35 | "environment-msfd-descriptors-criteria": [ | ||
35 | "d2-non-indigenous-species", | 36 | "d2-non-indigenous-species", | ||
36 | "d6-sea-floor-integrity-d1-biodiversity-benthic-habitats", | 37 | "d6-sea-floor-integrity-d1-biodiversity-benthic-habitats", | ||
37 | "d1c4-population-distributional-range-and-pattern" | 38 | "d1c4-population-distributional-range-and-pattern" | ||
38 | ], | 39 | ], | ||
39 | "environment-non-msfd-classes": [], | 40 | "environment-non-msfd-classes": [], | ||
40 | "environment-wfd": [ | 41 | "environment-wfd": [ | ||
41 | "ecological-status" | 42 | "ecological-status" | ||
42 | ], | 43 | ], | ||
43 | "groups": [], | 44 | "groups": [], | ||
44 | "id": "0d3b1c38-997e-48ec-be94-96b164f291da", | 45 | "id": "0d3b1c38-997e-48ec-be94-96b164f291da", | ||
45 | "isopen": false, | 46 | "isopen": false, | ||
46 | "language": "eng", | 47 | "language": "eng", | ||
47 | "legal-governance-planning-function": [], | 48 | "legal-governance-planning-function": [], | ||
48 | "legal-governance-planning-theme": [ | 49 | "legal-governance-planning-theme": [ | ||
49 | "environment-e-g-pollution-and-biodiversity", | 50 | "environment-e-g-pollution-and-biodiversity", | ||
50 | "conservation-i-e-protected-areas" | 51 | "conservation-i-e-protected-areas" | ||
51 | ], | 52 | ], | ||
52 | "legal-governance-planning-who-is-in-charge": "", | 53 | "legal-governance-planning-who-is-in-charge": "", | ||
53 | "license_id": "notspecified", | 54 | "license_id": "notspecified", | ||
54 | "license_title": "License not specified", | 55 | "license_title": "License not specified", | ||
55 | "maintainer": null, | 56 | "maintainer": null, | ||
56 | "maintainer_email": null, | 57 | "maintainer_email": null, | ||
57 | "maritime-activities": [], | 58 | "maritime-activities": [], | ||
58 | "metadata_completeness": "draft", | 59 | "metadata_completeness": "draft", | ||
59 | "metadata_created": "2025-03-28T16:16:25.205447", | 60 | "metadata_created": "2025-03-28T16:16:25.205447", | ||
t | 60 | "metadata_modified": "2025-06-10T00:57:22.693866", | t | 61 | "metadata_modified": "2025-08-08T08:30:14.027523", |
61 | "name": "probability-of-occurrence-caulerpa", | 62 | "name": "probability-of-occurrence-caulerpa", | ||
62 | "notes": "Annual probability of occurrence maps for Caulerpa | 63 | "notes": "Annual probability of occurrence maps for Caulerpa | ||
63 | cylindracea. The dataset covers the entire Mediterranean basin, even | 64 | cylindracea. The dataset covers the entire Mediterranean basin, even | ||
64 | if the predicted P of occurrence is limited to cover \"euphotic\" | 65 | if the predicted P of occurrence is limited to cover \"euphotic\" | ||
65 | zones (cells with depths greater than 200m are masked). Temporally, it | 66 | zones (cells with depths greater than 200m are masked). Temporally, it | ||
66 | spans from 2000 to 2050. For the future conditions (2020-2050) we | 67 | spans from 2000 to 2050. For the future conditions (2020-2050) we | ||
67 | follows the RCP8.5 projections scenario.\r\nThree possible | 68 | follows the RCP8.5 projections scenario.\r\nThree possible | ||
68 | classification thresholds can be applied, to provide a \"scenario | 69 | classification thresholds can be applied, to provide a \"scenario | ||
69 | exploration\". Methodology and results comes from the work of | 70 | exploration\". Methodology and results comes from the work of | ||
70 | Fianchini et al. (2025), still not available publicly.", | 71 | Fianchini et al. (2025), still not available publicly.", | ||
71 | "num_resources": 1, | 72 | "num_resources": 1, | ||
72 | "num_tags": 3, | 73 | "num_tags": 3, | ||
73 | "oceanographic-variables": [], | 74 | "oceanographic-variables": [], | ||
74 | "organization": { | 75 | "organization": { | ||
75 | "approval_status": "approved", | 76 | "approval_status": "approved", | ||
76 | "created": "2023-10-03T13:37:52.548819", | 77 | "created": "2023-10-03T13:37:52.548819", | ||
77 | "description": "Team for integration and updating of the Knowledge | 78 | "description": "Team for integration and updating of the Knowledge | ||
78 | Catalogue (metadata catalogue) for MSP on a national scale and | 79 | Catalogue (metadata catalogue) for MSP on a national scale and | ||
79 | Mediterranean projection, with a focus on safeguarding the | 80 | Mediterranean projection, with a focus on safeguarding the | ||
80 | biodiversity of marine ecosystems (Activity 4.1 Knowledge Catalogue | 81 | biodiversity of marine ecosystems (Activity 4.1 Knowledge Catalogue | ||
81 | for Biodiversity mainstreaming in Maritime Spatial Planning - | 82 | for Biodiversity mainstreaming in Maritime Spatial Planning - | ||
82 | MSP4BIODIVERSITY) within Spoke 2: Solutions to reverse marine | 83 | MSP4BIODIVERSITY) within Spoke 2: Solutions to reverse marine | ||
83 | biodiversity loss and manage marine resources sustainably of the | 84 | biodiversity loss and manage marine resources sustainably of the | ||
84 | __National Biodiversity Future Center \u2013 NBFC__\r\n\r\n", | 85 | __National Biodiversity Future Center \u2013 NBFC__\r\n\r\n", | ||
85 | "id": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | 86 | "id": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | ||
86 | "image_url": "2023-10-03-143557.861877LogoNBFCRGB.png", | 87 | "image_url": "2023-10-03-143557.861877LogoNBFCRGB.png", | ||
87 | "is_organization": true, | 88 | "is_organization": true, | ||
88 | "name": "msp-italy-working-team", | 89 | "name": "msp-italy-working-team", | ||
89 | "state": "active", | 90 | "state": "active", | ||
90 | "title": "MSP-Italy Working Team", | 91 | "title": "MSP-Italy Working Team", | ||
91 | "type": "organization" | 92 | "type": "organization" | ||
92 | }, | 93 | }, | ||
93 | "original-abstract": "The rapid spread of Invasive Alien Species | 94 | "original-abstract": "The rapid spread of Invasive Alien Species | ||
94 | (IAS) underlines the urgent need for predictive modelling to | 95 | (IAS) underlines the urgent need for predictive modelling to | ||
95 | accurately forecast future spread under climate change. Correlative | 96 | accurately forecast future spread under climate change. Correlative | ||
96 | Ecological Niche Models (ENMs) serve this purpose, but often struggle | 97 | Ecological Niche Models (ENMs) serve this purpose, but often struggle | ||
97 | with sampling bias, overfitting and uncertainty quantification and | 98 | with sampling bias, overfitting and uncertainty quantification and | ||
98 | rely on a certain degree of subjectivity, which limits their | 99 | rely on a certain degree of subjectivity, which limits their | ||
99 | reliability. We have developed an improved ENM framework using MaxEnt, | 100 | reliability. We have developed an improved ENM framework using MaxEnt, | ||
100 | that integrates standard and site-weighted performance metrics into a | 101 | that integrates standard and site-weighted performance metrics into a | ||
101 | multi-criteria decision process to select models that provide a better | 102 | multi-criteria decision process to select models that provide a better | ||
102 | balance between explanatory power and transferability. To detect | 103 | balance between explanatory power and transferability. To detect | ||
103 | overfitting, we introduced delta metrics that measure the dependence | 104 | overfitting, we introduced delta metrics that measure the dependence | ||
104 | of model performance on the weighting scheme. Furthermore, we | 105 | of model performance on the weighting scheme. Furthermore, we | ||
105 | performed a sensitivity analysis to quantify the classification | 106 | performed a sensitivity analysis to quantify the classification | ||
106 | uncertainty associated with different probability thresholds. We test | 107 | uncertainty associated with different probability thresholds. We test | ||
107 | this approach on Caulerpa cylindracea, one of the most dangerous IAS | 108 | this approach on Caulerpa cylindracea, one of the most dangerous IAS | ||
108 | in the Mediterranean. The selection approach identified an optimal | 109 | in the Mediterranean. The selection approach identified an optimal | ||
109 | model that showed high and stable performance across all weighting | 110 | model that showed high and stable performance across all weighting | ||
110 | schemes and multiple validation datasets. Both the annual and | 111 | schemes and multiple validation datasets. Both the annual and | ||
111 | scenario-based projections show a general shift towards lower habitat | 112 | scenario-based projections show a general shift towards lower habitat | ||
112 | suitability, with a statistically significant negative trend in High | 113 | suitability, with a statistically significant negative trend in High | ||
113 | Suitability areas. The decline suggests that the future spread of C. | 114 | Suitability areas. The decline suggests that the future spread of C. | ||
114 | cylindracea is likely to be limited to currently invaded areas, | 115 | cylindracea is likely to be limited to currently invaded areas, | ||
115 | assuming no adaptation. The high reliability of the model is supported | 116 | assuming no adaptation. The high reliability of the model is supported | ||
116 | by the extremely low extrapolation risk (0.21% of the predictions | 117 | by the extremely low extrapolation risk (0.21% of the predictions | ||
117 | under 'strict extrapolation') and the agreement of the response curves | 118 | under 'strict extrapolation') and the agreement of the response curves | ||
118 | with the known ecophysiology of the species. However, the sensitivity | 119 | with the known ecophysiology of the species. However, the sensitivity | ||
119 | analysis of threshold selection shows a non-uniform pattern of | 120 | analysis of threshold selection shows a non-uniform pattern of | ||
120 | classification uncertainty that appears to be related to invasion | 121 | classification uncertainty that appears to be related to invasion | ||
121 | stage, with the greatest variability observed in recently invaded | 122 | stage, with the greatest variability observed in recently invaded | ||
122 | regions such as the Northern Adriatic. Practical Implication: This | 123 | regions such as the Northern Adriatic. Practical Implication: This | ||
123 | framework provides robust predictions of invasion risk while | 124 | framework provides robust predictions of invasion risk while | ||
124 | explicitly quantifying uncertainty. The selection procedure, | 125 | explicitly quantifying uncertainty. The selection procedure, | ||
125 | leveraging delta metrics, explicitly include model generalisation | 126 | leveraging delta metrics, explicitly include model generalisation | ||
126 | ability in the ranking process. The annual suitability projections | 127 | ability in the ranking process. The annual suitability projections | ||
127 | enable temporal prioritization of control efforts. Threshold | 128 | enable temporal prioritization of control efforts. Threshold | ||
128 | sensitivity analysis identifies areas that require more conservative | 129 | sensitivity analysis identifies areas that require more conservative | ||
129 | management approaches, improving the quality and cost-effectiveness of | 130 | management approaches, improving the quality and cost-effectiveness of | ||
130 | intervention strategies.", | 131 | intervention strategies.", | ||
131 | "original-title": "Improving MaxEnt Reliability with Multi-Criteria | 132 | "original-title": "Improving MaxEnt Reliability with Multi-Criteria | ||
132 | Analysis and Site Weighting: A Case Study on Caulerpa cylindracea", | 133 | Analysis and Site Weighting: A Case Study on Caulerpa cylindracea", | ||
133 | "owner": "OGS", | 134 | "owner": "OGS", | ||
134 | "owner_org": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | 135 | "owner_org": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | ||
135 | "pdm_modules_relevance": [], | 136 | "pdm_modules_relevance": [], | ||
136 | "pdm_testing_relevance": [], | 137 | "pdm_testing_relevance": [], | ||
137 | "presentation_form": "map", | 138 | "presentation_form": "map", | ||
138 | "private": false, | 139 | "private": false, | ||
139 | "provider": "OGS", | 140 | "provider": "OGS", | ||
140 | "relationships_as_object": [], | 141 | "relationships_as_object": [], | ||
141 | "relationships_as_subject": [], | 142 | "relationships_as_subject": [], | ||
142 | "relevance-spatial-and-temporal": [ | 143 | "relevance-spatial-and-temporal": [ | ||
143 | "international-present-medium", | 144 | "international-present-medium", | ||
144 | "international-future-high", | 145 | "international-future-high", | ||
145 | "national-present-medium", | 146 | "national-present-medium", | ||
146 | "national-future-high", | 147 | "national-future-high", | ||
147 | "sub-area-present-medium", | 148 | "sub-area-present-medium", | ||
148 | "sub-area-future-medium", | 149 | "sub-area-future-medium", | ||
149 | "local-present-low", | 150 | "local-present-low", | ||
150 | "local-future-low" | 151 | "local-future-low" | ||
151 | ], | 152 | ], | ||
152 | "resources": [ | 153 | "resources": [ | ||
153 | { | 154 | { | ||
154 | "cache_last_updated": null, | 155 | "cache_last_updated": null, | ||
155 | "cache_url": null, | 156 | "cache_url": null, | ||
156 | "created": "2025-03-28T16:22:40.950809", | 157 | "created": "2025-03-28T16:22:40.950809", | ||
157 | "datastore_active": false, | 158 | "datastore_active": false, | ||
158 | "description": "Annual probability of occurrence maps for | 159 | "description": "Annual probability of occurrence maps for | ||
159 | C.cylindracea. 2000-2050", | 160 | C.cylindracea. 2000-2050", | ||
160 | "format": ".tif", | 161 | "format": ".tif", | ||
161 | "hash": "", | 162 | "hash": "", | ||
162 | "id": "73e28d39-40f1-458c-aa02-5b8533842520", | 163 | "id": "73e28d39-40f1-458c-aa02-5b8533842520", | ||
163 | "last_modified": "2025-03-28T16:35:35.346458", | 164 | "last_modified": "2025-03-28T16:35:35.346458", | ||
164 | "metadata_modified": "2025-03-28T16:35:35.365637", | 165 | "metadata_modified": "2025-03-28T16:35:35.365637", | ||
165 | "mimetype": "image/tiff", | 166 | "mimetype": "image/tiff", | ||
166 | "mimetype_inner": null, | 167 | "mimetype_inner": null, | ||
167 | "mspkc_resource_type": "GeospatialDataset", | 168 | "mspkc_resource_type": "GeospatialDataset", | ||
168 | "name": "annual_maps ", | 169 | "name": "annual_maps ", | ||
169 | "package_id": "0d3b1c38-997e-48ec-be94-96b164f291da", | 170 | "package_id": "0d3b1c38-997e-48ec-be94-96b164f291da", | ||
170 | "position": 0, | 171 | "position": 0, | ||
171 | "resource_type": null, | 172 | "resource_type": null, | ||
172 | "size": 9850345, | 173 | "size": 9850345, | ||
173 | "state": "active", | 174 | "state": "active", | ||
174 | "url": | 175 | "url": | ||
175 | /resource/73e28d39-40f1-458c-aa02-5b8533842520/download/p_annual.tif", | 176 | /resource/73e28d39-40f1-458c-aa02-5b8533842520/download/p_annual.tif", | ||
176 | "url_type": "upload" | 177 | "url_type": "upload" | ||
177 | } | 178 | } | ||
178 | ], | 179 | ], | ||
179 | "socio-economic-activities": [], | 180 | "socio-economic-activities": [], | ||
180 | "socio-economic-demography": [], | 181 | "socio-economic-demography": [], | ||
181 | "socio-economic-values": [], | 182 | "socio-economic-values": [], | ||
182 | "spatial_geojson": | 183 | "spatial_geojson": | ||
183 | 333333333,30.16666666666667],[-6.020833333333333,30.16666666666667]]]} | 184 | 333333333,30.16666666666667],[-6.020833333333333,30.16666666666667]]]} | ||
184 | ", | 185 | ", | ||
185 | "spatial_representation": "raster", | 186 | "spatial_representation": "raster", | ||
186 | "state": "active", | 187 | "state": "active", | ||
187 | "sub_category": "Invasive species", | 188 | "sub_category": "Invasive species", | ||
188 | "tags": [ | 189 | "tags": [ | ||
189 | { | 190 | { | ||
190 | "display_name": "OGS", | 191 | "display_name": "OGS", | ||
191 | "id": "a6ee2734-b0e3-404b-a300-0f8ef02f32dd", | 192 | "id": "a6ee2734-b0e3-404b-a300-0f8ef02f32dd", | ||
192 | "name": "OGS", | 193 | "name": "OGS", | ||
193 | "state": "active", | 194 | "state": "active", | ||
194 | "vocabulary_id": null | 195 | "vocabulary_id": null | ||
195 | }, | 196 | }, | ||
196 | { | 197 | { | ||
197 | "display_name": "mediterranean_sea", | 198 | "display_name": "mediterranean_sea", | ||
198 | "id": "781675ae-7e67-46ed-aadf-4fc3f1c4c655", | 199 | "id": "781675ae-7e67-46ed-aadf-4fc3f1c4c655", | ||
199 | "name": "mediterranean_sea", | 200 | "name": "mediterranean_sea", | ||
200 | "state": "active", | 201 | "state": "active", | ||
201 | "vocabulary_id": null | 202 | "vocabulary_id": null | ||
202 | }, | 203 | }, | ||
203 | { | 204 | { | ||
204 | "display_name": "types_of_habitat", | 205 | "display_name": "types_of_habitat", | ||
205 | "id": "948dd94f-4e01-4f6c-86c0-e48c85be7913", | 206 | "id": "948dd94f-4e01-4f6c-86c0-e48c85be7913", | ||
206 | "name": "types_of_habitat", | 207 | "name": "types_of_habitat", | ||
207 | "state": "active", | 208 | "state": "active", | ||
208 | "vocabulary_id": null | 209 | "vocabulary_id": null | ||
209 | } | 210 | } | ||
210 | ], | 211 | ], | ||
211 | "temporal_extent": "2000-01-01", | 212 | "temporal_extent": "2000-01-01", | ||
212 | "temporal_extent_end": "2050-12-31", | 213 | "temporal_extent_end": "2050-12-31", | ||
213 | "title": "2000-2050 Annual probability of occurrence maps for the | 214 | "title": "2000-2050 Annual probability of occurrence maps for the | ||
214 | invasive species: Caulerpa cylindracea", | 215 | invasive species: Caulerpa cylindracea", | ||
215 | "type": "msp-data", | 216 | "type": "msp-data", | ||
216 | "url": null, | 217 | "url": null, | ||
217 | "validation_level": "research", | 218 | "validation_level": "research", | ||
218 | "version": null, | 219 | "version": null, | ||
219 | "web_services": [], | 220 | "web_services": [], | ||
220 | "web_services_other": "" | 221 | "web_services_other": "" | ||
221 | } | 222 | } |