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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": "", | ||
9 | "clusters": [ | 9 | "clusters": [ | ||
10 | "environment", | 10 | "environment", | ||
11 | "coastal-land-use-and-planning", | 11 | "coastal-land-use-and-planning", | ||
12 | "legal-governance-planning" | 12 | "legal-governance-planning" | ||
13 | ], | 13 | ], | ||
14 | "coastal-land-use-and-planning": [ | 14 | "coastal-land-use-and-planning": [ | ||
15 | "planning-strategic-national-eu-regulated", | 15 | "planning-strategic-national-eu-regulated", | ||
16 | "planning-strategic-national-others", | 16 | "planning-strategic-national-others", | ||
17 | "planning-strategic-subnational", | 17 | "planning-strategic-subnational", | ||
18 | "planning-strategic-local", | 18 | "planning-strategic-local", | ||
19 | "planning-coordination-sub-national", | 19 | "planning-coordination-sub-national", | ||
20 | "planning-operational-sub-national" | 20 | "planning-operational-sub-national" | ||
21 | ], | 21 | ], | ||
22 | "conservation-types": [], | 22 | "conservation-types": [], | ||
23 | "creator_user_id": "c1526409-0a5f-4f99-9221-d0b97cff0942", | 23 | "creator_user_id": "c1526409-0a5f-4f99-9221-d0b97cff0942", | ||
24 | "crs": [ | 24 | "crs": [ | ||
25 | "other" | 25 | "other" | ||
26 | ], | 26 | ], | ||
27 | "crs_other": "", | 27 | "crs_other": "", | ||
28 | "data_accessibility": "Data available on request. Article still not | 28 | "data_accessibility": "Data available on request. Article still not | ||
29 | published so avoid external sharing. contact mfianchini@ogs.it", | 29 | published so avoid external sharing. contact mfianchini@ogs.it", | ||
30 | "data_portal": "", | 30 | "data_portal": "", | ||
31 | "derived": "", | 31 | "derived": "", | ||
32 | "derives_from_string": "", | 32 | "derives_from_string": "", | ||
33 | "domain_area": "mediterranean_sea", | 33 | "domain_area": "mediterranean_sea", | ||
34 | "ecosystem-services": [], | 34 | "ecosystem-services": [], | ||
35 | "environment-msfd-classes": [ | 35 | "environment-msfd-classes": [ | ||
36 | "habitats-seabed", | 36 | "habitats-seabed", | ||
37 | "pressure-biological-input-or-spread-of-non-indigenous-species" | 37 | "pressure-biological-input-or-spread-of-non-indigenous-species" | ||
38 | ], | 38 | ], | ||
39 | "environment-msfd-descriptors-criteria": [ | 39 | "environment-msfd-descriptors-criteria": [ | ||
40 | "d2-non-indigenous-species", | 40 | "d2-non-indigenous-species", | ||
41 | "d6-sea-floor-integrity-d1-biodiversity-benthic-habitats", | 41 | "d6-sea-floor-integrity-d1-biodiversity-benthic-habitats", | ||
42 | "d1c4-population-distributional-range-and-pattern" | 42 | "d1c4-population-distributional-range-and-pattern" | ||
43 | ], | 43 | ], | ||
44 | "environment-non-msfd-classes": [], | 44 | "environment-non-msfd-classes": [], | ||
45 | "environment-wfd": [ | 45 | "environment-wfd": [ | ||
46 | "ecological-status" | 46 | "ecological-status" | ||
47 | ], | 47 | ], | ||
48 | "groups": [], | 48 | "groups": [], | ||
49 | "id": "0d3b1c38-997e-48ec-be94-96b164f291da", | 49 | "id": "0d3b1c38-997e-48ec-be94-96b164f291da", | ||
50 | "isopen": false, | 50 | "isopen": false, | ||
51 | "language": "eng", | 51 | "language": "eng", | ||
52 | "legal-governance-planning-function": [], | 52 | "legal-governance-planning-function": [], | ||
53 | "legal-governance-planning-theme": [ | 53 | "legal-governance-planning-theme": [ | ||
54 | "environment-e-g-pollution-and-biodiversity", | 54 | "environment-e-g-pollution-and-biodiversity", | ||
55 | "conservation-i-e-protected-areas" | 55 | "conservation-i-e-protected-areas" | ||
56 | ], | 56 | ], | ||
57 | "legal-governance-planning-who-is-in-charge": "", | 57 | "legal-governance-planning-who-is-in-charge": "", | ||
58 | "license_id": "notspecified", | 58 | "license_id": "notspecified", | ||
59 | "license_title": "License not specified", | 59 | "license_title": "License not specified", | ||
60 | "maintainer": null, | 60 | "maintainer": null, | ||
61 | "maintainer_email": null, | 61 | "maintainer_email": null, | ||
62 | "maritime-activities": [], | 62 | "maritime-activities": [], | ||
63 | "metadata_completeness": "draft", | 63 | "metadata_completeness": "draft", | ||
64 | "metadata_created": "2025-03-28T16:16:25.205447", | 64 | "metadata_created": "2025-03-28T16:16:25.205447", | ||
t | 65 | "metadata_modified": "2025-08-08T08:50:51.881577", | t | 65 | "metadata_modified": "2025-08-08T09:07:52.128835", |
66 | "name": "probability-of-occurrence-caulerpa", | 66 | "name": "probability-of-occurrence-caulerpa", | ||
67 | "notes": "Annual probability of occurrence maps for Caulerpa | 67 | "notes": "Annual probability of occurrence maps for Caulerpa | ||
68 | cylindracea. The dataset covers the entire Mediterranean basin, even | 68 | cylindracea. The dataset covers the entire Mediterranean basin, even | ||
69 | if the predicted P of occurrence is limited to cover \"euphotic\" | 69 | if the predicted P of occurrence is limited to cover \"euphotic\" | ||
70 | zones (cells with depths greater than 200m are masked). Temporally, it | 70 | zones (cells with depths greater than 200m are masked). Temporally, it | ||
71 | spans from 2000 to 2050. For the future conditions (2020-2050) we | 71 | spans from 2000 to 2050. For the future conditions (2020-2050) we | ||
72 | follows the RCP8.5 projections scenario.\r\nThree possible | 72 | follows the RCP8.5 projections scenario.\r\nThree possible | ||
73 | classification thresholds can be applied, to provide a \"scenario | 73 | classification thresholds can be applied, to provide a \"scenario | ||
74 | exploration\". Methodology and results comes from the work of | 74 | exploration\". Methodology and results comes from the work of | ||
75 | Fianchini et al. (2025), still not available publicly.", | 75 | Fianchini et al. (2025), still not available publicly.", | ||
76 | "num_resources": 1, | 76 | "num_resources": 1, | ||
77 | "num_tags": 3, | 77 | "num_tags": 3, | ||
78 | "oceanographic-variables": [], | 78 | "oceanographic-variables": [], | ||
79 | "organization": { | 79 | "organization": { | ||
80 | "approval_status": "approved", | 80 | "approval_status": "approved", | ||
81 | "created": "2023-10-03T13:37:52.548819", | 81 | "created": "2023-10-03T13:37:52.548819", | ||
82 | "description": "Team for integration and updating of the Knowledge | 82 | "description": "Team for integration and updating of the Knowledge | ||
83 | Catalogue (metadata catalogue) for MSP on a national scale and | 83 | Catalogue (metadata catalogue) for MSP on a national scale and | ||
84 | Mediterranean projection, with a focus on safeguarding the | 84 | Mediterranean projection, with a focus on safeguarding the | ||
85 | biodiversity of marine ecosystems (Activity 4.1 Knowledge Catalogue | 85 | biodiversity of marine ecosystems (Activity 4.1 Knowledge Catalogue | ||
86 | for Biodiversity mainstreaming in Maritime Spatial Planning - | 86 | for Biodiversity mainstreaming in Maritime Spatial Planning - | ||
87 | MSP4BIODIVERSITY) within Spoke 2: Solutions to reverse marine | 87 | MSP4BIODIVERSITY) within Spoke 2: Solutions to reverse marine | ||
88 | biodiversity loss and manage marine resources sustainably of the | 88 | biodiversity loss and manage marine resources sustainably of the | ||
89 | __National Biodiversity Future Center \u2013 NBFC__\r\n\r\n", | 89 | __National Biodiversity Future Center \u2013 NBFC__\r\n\r\n", | ||
90 | "id": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | 90 | "id": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | ||
91 | "image_url": "2023-10-03-143557.861877LogoNBFCRGB.png", | 91 | "image_url": "2023-10-03-143557.861877LogoNBFCRGB.png", | ||
92 | "is_organization": true, | 92 | "is_organization": true, | ||
93 | "name": "msp-italy-working-team", | 93 | "name": "msp-italy-working-team", | ||
94 | "state": "active", | 94 | "state": "active", | ||
95 | "title": "MSP-Italy Working Team", | 95 | "title": "MSP-Italy Working Team", | ||
96 | "type": "organization" | 96 | "type": "organization" | ||
97 | }, | 97 | }, | ||
98 | "original-abstract": "The rapid spread of Invasive Alien Species | 98 | "original-abstract": "The rapid spread of Invasive Alien Species | ||
99 | (IAS) underlines the urgent need for predictive modelling to | 99 | (IAS) underlines the urgent need for predictive modelling to | ||
100 | accurately forecast future spread under climate change. Correlative | 100 | accurately forecast future spread under climate change. Correlative | ||
101 | Ecological Niche Models (ENMs) serve this purpose, but often struggle | 101 | Ecological Niche Models (ENMs) serve this purpose, but often struggle | ||
102 | with sampling bias, overfitting and uncertainty quantification and | 102 | with sampling bias, overfitting and uncertainty quantification and | ||
103 | rely on a certain degree of subjectivity, which limits their | 103 | rely on a certain degree of subjectivity, which limits their | ||
104 | reliability. We have developed an improved ENM framework using MaxEnt, | 104 | reliability. We have developed an improved ENM framework using MaxEnt, | ||
105 | that integrates standard and site-weighted performance metrics into a | 105 | that integrates standard and site-weighted performance metrics into a | ||
106 | multi-criteria decision process to select models that provide a better | 106 | multi-criteria decision process to select models that provide a better | ||
107 | balance between explanatory power and transferability. To detect | 107 | balance between explanatory power and transferability. To detect | ||
108 | overfitting, we introduced delta metrics that measure the dependence | 108 | overfitting, we introduced delta metrics that measure the dependence | ||
109 | of model performance on the weighting scheme. Furthermore, we | 109 | of model performance on the weighting scheme. Furthermore, we | ||
110 | performed a sensitivity analysis to quantify the classification | 110 | performed a sensitivity analysis to quantify the classification | ||
111 | uncertainty associated with different probability thresholds. We test | 111 | uncertainty associated with different probability thresholds. We test | ||
112 | this approach on Caulerpa cylindracea, one of the most dangerous IAS | 112 | this approach on Caulerpa cylindracea, one of the most dangerous IAS | ||
113 | in the Mediterranean. The selection approach identified an optimal | 113 | in the Mediterranean. The selection approach identified an optimal | ||
114 | model that showed high and stable performance across all weighting | 114 | model that showed high and stable performance across all weighting | ||
115 | schemes and multiple validation datasets. Both the annual and | 115 | schemes and multiple validation datasets. Both the annual and | ||
116 | scenario-based projections show a general shift towards lower habitat | 116 | scenario-based projections show a general shift towards lower habitat | ||
117 | suitability, with a statistically significant negative trend in High | 117 | suitability, with a statistically significant negative trend in High | ||
118 | Suitability areas. The decline suggests that the future spread of C. | 118 | Suitability areas. The decline suggests that the future spread of C. | ||
119 | cylindracea is likely to be limited to currently invaded areas, | 119 | cylindracea is likely to be limited to currently invaded areas, | ||
120 | assuming no adaptation. The high reliability of the model is supported | 120 | assuming no adaptation. The high reliability of the model is supported | ||
121 | by the extremely low extrapolation risk (0.21% of the predictions | 121 | by the extremely low extrapolation risk (0.21% of the predictions | ||
122 | under 'strict extrapolation') and the agreement of the response curves | 122 | under 'strict extrapolation') and the agreement of the response curves | ||
123 | with the known ecophysiology of the species. However, the sensitivity | 123 | with the known ecophysiology of the species. However, the sensitivity | ||
124 | analysis of threshold selection shows a non-uniform pattern of | 124 | analysis of threshold selection shows a non-uniform pattern of | ||
125 | classification uncertainty that appears to be related to invasion | 125 | classification uncertainty that appears to be related to invasion | ||
126 | stage, with the greatest variability observed in recently invaded | 126 | stage, with the greatest variability observed in recently invaded | ||
127 | regions such as the Northern Adriatic. Practical Implication: This | 127 | regions such as the Northern Adriatic. Practical Implication: This | ||
128 | framework provides robust predictions of invasion risk while | 128 | framework provides robust predictions of invasion risk while | ||
129 | explicitly quantifying uncertainty. The selection procedure, | 129 | explicitly quantifying uncertainty. The selection procedure, | ||
130 | leveraging delta metrics, explicitly include model generalisation | 130 | leveraging delta metrics, explicitly include model generalisation | ||
131 | ability in the ranking process. The annual suitability projections | 131 | ability in the ranking process. The annual suitability projections | ||
132 | enable temporal prioritization of control efforts. Threshold | 132 | enable temporal prioritization of control efforts. Threshold | ||
133 | sensitivity analysis identifies areas that require more conservative | 133 | sensitivity analysis identifies areas that require more conservative | ||
134 | management approaches, improving the quality and cost-effectiveness of | 134 | management approaches, improving the quality and cost-effectiveness of | ||
135 | intervention strategies.", | 135 | intervention strategies.", | ||
136 | "original-title": "Improving MaxEnt Reliability with Multi-Criteria | 136 | "original-title": "Improving MaxEnt Reliability with Multi-Criteria | ||
137 | Analysis and Site Weighting: A Case Study on Caulerpa cylindracea", | 137 | Analysis and Site Weighting: A Case Study on Caulerpa cylindracea", | ||
138 | "owner": "OGS", | 138 | "owner": "OGS", | ||
139 | "owner_org": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | 139 | "owner_org": "8ed582af-8314-4998-b7e4-9de7cd1975dd", | ||
140 | "pdm_modules_relevance": [], | 140 | "pdm_modules_relevance": [], | ||
141 | "pdm_testing_relevance": [], | 141 | "pdm_testing_relevance": [], | ||
142 | "presentation_form": "map", | 142 | "presentation_form": "map", | ||
143 | "private": false, | 143 | "private": false, | ||
144 | "provider": "OGS", | 144 | "provider": "OGS", | ||
145 | "relationships_as_object": [], | 145 | "relationships_as_object": [], | ||
146 | "relationships_as_subject": [], | 146 | "relationships_as_subject": [], | ||
147 | "relevance-spatial-and-temporal": [ | 147 | "relevance-spatial-and-temporal": [ | ||
148 | "international-present-medium", | 148 | "international-present-medium", | ||
149 | "international-future-high", | 149 | "international-future-high", | ||
150 | "national-present-medium", | 150 | "national-present-medium", | ||
151 | "national-future-high", | 151 | "national-future-high", | ||
152 | "sub-area-present-medium", | 152 | "sub-area-present-medium", | ||
153 | "sub-area-future-medium", | 153 | "sub-area-future-medium", | ||
154 | "local-present-low", | 154 | "local-present-low", | ||
155 | "local-future-low" | 155 | "local-future-low" | ||
156 | ], | 156 | ], | ||
157 | "resources": [ | 157 | "resources": [ | ||
158 | { | 158 | { | ||
159 | "cache_last_updated": null, | 159 | "cache_last_updated": null, | ||
160 | "cache_url": null, | 160 | "cache_url": null, | ||
161 | "created": "2025-03-28T16:22:40.950809", | 161 | "created": "2025-03-28T16:22:40.950809", | ||
162 | "datastore_active": false, | 162 | "datastore_active": false, | ||
163 | "description": "Annual probability of occurrence maps for | 163 | "description": "Annual probability of occurrence maps for | ||
164 | C.cylindracea. 2000-2050", | 164 | C.cylindracea. 2000-2050", | ||
165 | "format": ".tif", | 165 | "format": ".tif", | ||
166 | "hash": "", | 166 | "hash": "", | ||
167 | "id": "73e28d39-40f1-458c-aa02-5b8533842520", | 167 | "id": "73e28d39-40f1-458c-aa02-5b8533842520", | ||
168 | "last_modified": "2025-03-28T16:35:35.346458", | 168 | "last_modified": "2025-03-28T16:35:35.346458", | ||
169 | "metadata_modified": "2025-03-28T16:35:35.365637", | 169 | "metadata_modified": "2025-03-28T16:35:35.365637", | ||
170 | "mimetype": "image/tiff", | 170 | "mimetype": "image/tiff", | ||
171 | "mimetype_inner": null, | 171 | "mimetype_inner": null, | ||
172 | "mspkc_resource_type": "GeospatialDataset", | 172 | "mspkc_resource_type": "GeospatialDataset", | ||
173 | "name": "annual_maps ", | 173 | "name": "annual_maps ", | ||
174 | "package_id": "0d3b1c38-997e-48ec-be94-96b164f291da", | 174 | "package_id": "0d3b1c38-997e-48ec-be94-96b164f291da", | ||
175 | "position": 0, | 175 | "position": 0, | ||
176 | "resource_type": null, | 176 | "resource_type": null, | ||
177 | "size": 9850345, | 177 | "size": 9850345, | ||
178 | "state": "active", | 178 | "state": "active", | ||
179 | "url": | 179 | "url": | ||
180 | /resource/73e28d39-40f1-458c-aa02-5b8533842520/download/p_annual.tif", | 180 | /resource/73e28d39-40f1-458c-aa02-5b8533842520/download/p_annual.tif", | ||
181 | "url_type": "upload" | 181 | "url_type": "upload" | ||
182 | } | 182 | } | ||
183 | ], | 183 | ], | ||
184 | "socio-economic-activities": [], | 184 | "socio-economic-activities": [], | ||
185 | "socio-economic-demography": [], | 185 | "socio-economic-demography": [], | ||
186 | "socio-economic-values": [], | 186 | "socio-economic-values": [], | ||
187 | "spatial_geojson": | 187 | "spatial_geojson": | ||
188 | 333333333,30.16666666666667],[-6.020833333333333,30.16666666666667]]]} | 188 | 333333333,30.16666666666667],[-6.020833333333333,30.16666666666667]]]} | ||
189 | ", | 189 | ", | ||
190 | "spatial_representation": "raster", | 190 | "spatial_representation": "raster", | ||
191 | "state": "active", | 191 | "state": "active", | ||
192 | "sub_category": "Invasive species", | 192 | "sub_category": "Invasive species", | ||
193 | "tags": [ | 193 | "tags": [ | ||
194 | { | 194 | { | ||
195 | "display_name": "OGS", | 195 | "display_name": "OGS", | ||
196 | "id": "a6ee2734-b0e3-404b-a300-0f8ef02f32dd", | 196 | "id": "a6ee2734-b0e3-404b-a300-0f8ef02f32dd", | ||
197 | "name": "OGS", | 197 | "name": "OGS", | ||
198 | "state": "active", | 198 | "state": "active", | ||
199 | "vocabulary_id": null | 199 | "vocabulary_id": null | ||
200 | }, | 200 | }, | ||
201 | { | 201 | { | ||
202 | "display_name": "mediterranean_sea", | 202 | "display_name": "mediterranean_sea", | ||
203 | "id": "781675ae-7e67-46ed-aadf-4fc3f1c4c655", | 203 | "id": "781675ae-7e67-46ed-aadf-4fc3f1c4c655", | ||
204 | "name": "mediterranean_sea", | 204 | "name": "mediterranean_sea", | ||
205 | "state": "active", | 205 | "state": "active", | ||
206 | "vocabulary_id": null | 206 | "vocabulary_id": null | ||
207 | }, | 207 | }, | ||
208 | { | 208 | { | ||
209 | "display_name": "types_of_habitat", | 209 | "display_name": "types_of_habitat", | ||
210 | "id": "948dd94f-4e01-4f6c-86c0-e48c85be7913", | 210 | "id": "948dd94f-4e01-4f6c-86c0-e48c85be7913", | ||
211 | "name": "types_of_habitat", | 211 | "name": "types_of_habitat", | ||
212 | "state": "active", | 212 | "state": "active", | ||
213 | "vocabulary_id": null | 213 | "vocabulary_id": null | ||
214 | } | 214 | } | ||
215 | ], | 215 | ], | ||
216 | "temporal_extent": "2000-01-01", | 216 | "temporal_extent": "2000-01-01", | ||
217 | "temporal_extent_end": "2050-12-31", | 217 | "temporal_extent_end": "2050-12-31", | ||
218 | "title": "2000-2050 Annual probability of occurrence maps for the | 218 | "title": "2000-2050 Annual probability of occurrence maps for the | ||
219 | invasive species: Caulerpa cylindracea", | 219 | invasive species: Caulerpa cylindracea", | ||
220 | "type": "msp-data", | 220 | "type": "msp-data", | ||
221 | "url": null, | 221 | "url": null, | ||
222 | "validation_level": "research", | 222 | "validation_level": "research", | ||
223 | "version": null, | 223 | "version": null, | ||
224 | "web_services": [], | 224 | "web_services": [], | ||
225 | "web_services_other": "" | 225 | "web_services_other": "" | ||
226 | } | 226 | } |