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| f | 1 | { | f | 1 | { |
| 2 | "access_rights": | 2 | "access_rights": | ||
| 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | ||
| 4 | "alternate_identifier": "ISBN: 978-91-637-7327-3", | 4 | "alternate_identifier": "ISBN: 978-91-637-7327-3", | ||
| 5 | "author": "Rosell, C., B\u00edl, M., Camps, F., Andrasik, R., | 5 | "author": "Rosell, C., B\u00edl, M., Camps, F., Andrasik, R., | ||
| 6 | Fern\u00e1ndez-Bou, M. y Janoska, Z.", | 6 | Fern\u00e1ndez-Bou, M. y Janoska, Z.", | ||
| 7 | "author_name": "Rosell, C., B\u00edl, M., Camps, F., Andrasik, R., | 7 | "author_name": "Rosell, C., B\u00edl, M., Camps, F., Andrasik, R., | ||
| 8 | Fern\u00e1ndez-Bou, M. y Janoska, Z.", | 8 | Fern\u00e1ndez-Bou, M. y Janoska, Z.", | ||
| 9 | "classification_variables": { | 9 | "classification_variables": { | ||
| 10 | "es": "" | 10 | "es": "" | ||
| 11 | }, | 11 | }, | ||
| 12 | "conforms_to": [ | 12 | "conforms_to": [ | ||
| 13 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | 13 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | ||
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| 15 | "contact": [ | 15 | "contact": [ | ||
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| 18 | "name": "Organismo publicador del Cat\u00e1logo", | 18 | "name": "Organismo publicador del Cat\u00e1logo", | ||
| 19 | "role": | 19 | "role": | ||
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| 23 | "url": "https://organismo.example.org/" | 23 | "url": "https://organismo.example.org/" | ||
| 24 | } | 24 | } | ||
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| 26 | "contact_email": "organismo@example.org", | 26 | "contact_email": "organismo@example.org", | ||
| 27 | "contact_name": "Organismo publicador del Cat\u00e1logo", | 27 | "contact_name": "Organismo publicador del Cat\u00e1logo", | ||
| 28 | "contact_role": | 28 | "contact_role": | ||
| 29 | e.ec.europa.eu/metadata-codelist/ResponsiblePartyRole/pointOfContact", | 29 | e.ec.europa.eu/metadata-codelist/ResponsiblePartyRole/pointOfContact", | ||
| 30 | "contact_uri": | 30 | "contact_uri": | ||
| 31 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | 31 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | ||
| 32 | "contact_url": "https://organismo.example.org/", | 32 | "contact_url": "https://organismo.example.org/", | ||
| 33 | "created": "2025-05-23", | 33 | "created": "2025-05-23", | ||
| 34 | "creator": [ | 34 | "creator": [ | ||
| 35 | { | 35 | { | ||
| 36 | "name": "Rosell, C., B\u00edl, M., Camps, F., Andrasik, R., | 36 | "name": "Rosell, C., B\u00edl, M., Camps, F., Andrasik, R., | ||
| 37 | Fern\u00e1ndez-Bou, M. y Janoska, Z." | 37 | Fern\u00e1ndez-Bou, M. y Janoska, Z." | ||
| 38 | } | 38 | } | ||
| 39 | ], | 39 | ], | ||
| 40 | "creator_user_id": "d24a314a-79ce-48c0-abd9-54cb42706da4", | 40 | "creator_user_id": "d24a314a-79ce-48c0-abd9-54cb42706da4", | ||
| 41 | "dataset_scope": "non_spatial_dataset", | 41 | "dataset_scope": "non_spatial_dataset", | ||
| 42 | "dcat_type": "http://purl.org/dc/dcmitype/Text", | 42 | "dcat_type": "http://purl.org/dc/dcmitype/Text", | ||
| 43 | "encoding": "UTF-8", | 43 | "encoding": "UTF-8", | ||
| 44 | "featured": false, | 44 | "featured": false, | ||
| 45 | "graphic_overview": | 45 | "graphic_overview": | ||
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| 47 | "groups": [ | 47 | "groups": [ | ||
| 48 | { | 48 | { | ||
| 49 | "description": "La fragmentaci\u00f3n del h\u00e1bitat se define | 49 | "description": "La fragmentaci\u00f3n del h\u00e1bitat se define | ||
| 50 | como el proceso durante el cual una gran extensi\u00f3n de | 50 | como el proceso durante el cual una gran extensi\u00f3n de | ||
| 51 | h\u00e1bitat se transforma en una serie de parches m\u00e1s | 51 | h\u00e1bitat se transforma en una serie de parches m\u00e1s | ||
| 52 | peque\u00f1os de menor superficie total aislados entre s\u00ed por una | 52 | peque\u00f1os de menor superficie total aislados entre s\u00ed por una | ||
| 53 | matriz de h\u00e1bitats distinta de la original", | 53 | matriz de h\u00e1bitats distinta de la original", | ||
| 54 | "display_name": "Fragmentaci\u00f3n del h\u00e1bitat", | 54 | "display_name": "Fragmentaci\u00f3n del h\u00e1bitat", | ||
| 55 | "id": "10439641-6830-4144-a3ab-117add931cd5", | 55 | "id": "10439641-6830-4144-a3ab-117add931cd5", | ||
| 56 | "image_display_url": | 56 | "image_display_url": | ||
| 57 | e_2010_UE_Illustr.jpg/320px-Green_infrastructure_2010_UE_Illustr.jpg", | 57 | e_2010_UE_Illustr.jpg/320px-Green_infrastructure_2010_UE_Illustr.jpg", | ||
| 58 | "name": "fragmentacion-habitat", | 58 | "name": "fragmentacion-habitat", | ||
| 59 | "title": "Fragmentaci\u00f3n del h\u00e1bitat" | 59 | "title": "Fragmentaci\u00f3n del h\u00e1bitat" | ||
| 60 | } | 60 | } | ||
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| 62 | "hvd": "non_hvd", | 62 | "hvd": "non_hvd", | ||
| 63 | "id": "f3cd2a6f-df57-5303-bf46-bad842a3d019", | 63 | "id": "f3cd2a6f-df57-5303-bf46-bad842a3d019", | ||
| 64 | "identifier": "f3cd2a6f-df57-5303-bf46-bad842a3d019", | 64 | "identifier": "f3cd2a6f-df57-5303-bf46-bad842a3d019", | ||
| 65 | "inspire_id": "", | 65 | "inspire_id": "", | ||
| 66 | "isopen": true, | 66 | "isopen": true, | ||
| 67 | "language": | 67 | "language": | ||
| 68 | "http://publications.europa.eu/resource/authority/language/SPA", | 68 | "http://publications.europa.eu/resource/authority/language/SPA", | ||
| 69 | "license_id": "cc-by", | 69 | "license_id": "cc-by", | ||
| 70 | "license_title": "Creative Commons Attribution", | 70 | "license_title": "Creative Commons Attribution", | ||
| 71 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 71 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
| 72 | "lineage_process_steps": [], | 72 | "lineage_process_steps": [], | ||
| 73 | "lineage_source": [ | 73 | "lineage_source": [ | ||
| 74 | "2014 IENE International Conference. Programme and abstracts", | 74 | "2014 IENE International Conference. Programme and abstracts", | ||
| 75 | "pag. 76" | 75 | "pag. 76" | ||
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| 77 | "maintainer": "", | 77 | "maintainer": "", | ||
| 78 | "maintainer_name": "", | 78 | "maintainer_name": "", | ||
| 79 | "metadata_created": "2026-06-23T14:47:39.629563", | 79 | "metadata_created": "2026-06-23T14:47:39.629563", | ||
| n | 80 | "metadata_modified": "2026-06-25T12:21:36.759690", | n | 80 | "metadata_modified": "2026-06-25T12:25:44.719166", |
| 81 | "metadata_profile": [ | 81 | "metadata_profile": [ | ||
| 82 | "https://www.w3.org/TR/vocab-dcat-3/" | 82 | "https://www.w3.org/TR/vocab-dcat-3/" | ||
| 83 | ], | 83 | ], | ||
| 84 | "miteco_data_population": { | 84 | "miteco_data_population": { | ||
| 85 | "es": "" | 85 | "es": "" | ||
| 86 | }, | 86 | }, | ||
| 87 | "miteco_data_territory": { | 87 | "miteco_data_territory": { | ||
| 88 | "es": "" | 88 | "es": "" | ||
| 89 | }, | 89 | }, | ||
| 90 | "miteco_dataset_type": | 90 | "miteco_dataset_type": | ||
| 91 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 91 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 92 | "miteco_geo_level": "1", | 92 | "miteco_geo_level": "1", | ||
| 93 | "modified": "2026-06-25", | 93 | "modified": "2026-06-25", | ||
| 94 | "name": "f3cd2a6f-df57-5303-bf46-bad842a3d019", | 94 | "name": "f3cd2a6f-df57-5303-bf46-bad842a3d019", | ||
| 95 | "notes": "Animal Vehicle Collisions (AVC) often show a pattern of | 95 | "notes": "Animal Vehicle Collisions (AVC) often show a pattern of | ||
| 96 | aggregation, with clusters along conflictive road stretches. Road | 96 | aggregation, with clusters along conflictive road stretches. Road | ||
| 97 | traffic safety is diminished in these hotspots, due to the risk of | 97 | traffic safety is diminished in these hotspots, due to the risk of | ||
| 98 | accidents involving animals. Therefore, the identification of these | 98 | accidents involving animals. Therefore, the identification of these | ||
| 99 | stretches is essential to apply effective mitigation measures. Data | 99 | stretches is essential to apply effective mitigation measures. Data | ||
| 100 | from 2,110 accidents involving ungulates were registered in the 12,124 | 100 | from 2,110 accidents involving ungulates were registered in the 12,124 | ||
| 101 | km of the Catalan (NE Spain) road network during a five-year period | 101 | km of the Catalan (NE Spain) road network during a five-year period | ||
| 102 | (2007-2011). The data were collected by traffic police and completed | 102 | (2007-2011). The data were collected by traffic police and completed | ||
| 103 | with data provided by road management teams, the traffic management | 103 | with data provided by road management teams, the traffic management | ||
| 104 | agency and the wildlife management department. Two different methods | 104 | agency and the wildlife management department. Two different methods | ||
| 105 | were used to determine the location of the clusters of accidents | 105 | were used to determine the location of the clusters of accidents | ||
| 106 | caused by ungulates. First the kernel density estimation (KDE) was | 106 | caused by ungulates. First the kernel density estimation (KDE) was | ||
| 107 | applied to the 1-km stretches of road that had previously been | 107 | applied to the 1-km stretches of road that had previously been | ||
| 108 | identified as the most conflictive by comparing the data with a random | 108 | identified as the most conflictive by comparing the data with a random | ||
| 109 | situation in which the probability of occurrence along each stretch | 109 | situation in which the probability of occurrence along each stretch | ||
| 110 | followed a Poisson distribution. However, this method could not be | 110 | followed a Poisson distribution. However, this method could not be | ||
| 111 | used to determine the statistical significance of the clusters that | 111 | used to determine the statistical significance of the clusters that | ||
| 112 | were identified. The second method (KDE+) consisted of a procedure | 112 | were identified. The second method (KDE+) consisted of a procedure | ||
| 113 | based on standard KDE that identify the most hazardous road stretches | 113 | based on standard KDE that identify the most hazardous road stretches | ||
| 114 | by testing the statistical significance of the resulting clusters. The | 114 | by testing the statistical significance of the resulting clusters. The | ||
| 115 | clusters were identified where the kernel density function exceeded | 115 | clusters were identified where the kernel density function exceeded | ||
| 116 | the significance level corresponding to the 95th percentile, and the | 116 | the significance level corresponding to the 95th percentile, and the | ||
| 117 | application of cluster strength evaluation provided a sorted list of | 117 | application of cluster strength evaluation provided a sorted list of | ||
| 118 | hazardous locations. Traffic accidents caused by ungulates mainly wild | 118 | hazardous locations. Traffic accidents caused by ungulates mainly wild | ||
| 119 | boar and deer) have a strong tendency to cluster, with about one third | 119 | boar and deer) have a strong tendency to cluster, with about one third | ||
| 120 | of accidents located at around 1% of the road network length. The | 120 | of accidents located at around 1% of the road network length. The | ||
| 121 | results provided by this method allow efforts to apply mitigation | 121 | results provided by this method allow efforts to apply mitigation | ||
| 122 | measures to be focused on the most hazardous road stretches, where the | 122 | measures to be focused on the most hazardous road stretches, where the | ||
| 123 | best benefit-cost ratio can be expected.", | 123 | best benefit-cost ratio can be expected.", | ||
| 124 | "notes_translated": { | 124 | "notes_translated": { | ||
| 125 | "en": "Animal Vehicle Collisions (AVC) often show a pattern of | 125 | "en": "Animal Vehicle Collisions (AVC) often show a pattern of | ||
| 126 | aggregation, with clusters along conflictive road stretches. Road | 126 | aggregation, with clusters along conflictive road stretches. Road | ||
| 127 | traffic safety is diminished in these hotspots, due to the risk of | 127 | traffic safety is diminished in these hotspots, due to the risk of | ||
| 128 | accidents involving animals. Therefore, the identification of these | 128 | accidents involving animals. Therefore, the identification of these | ||
| 129 | stretches is essential to apply effective mitigation measures. Data | 129 | stretches is essential to apply effective mitigation measures. Data | ||
| 130 | from 2,110 accidents involving ungulates were registered in the 12,124 | 130 | from 2,110 accidents involving ungulates were registered in the 12,124 | ||
| 131 | km of the Catalan (NE Spain) road network during a five-year period | 131 | km of the Catalan (NE Spain) road network during a five-year period | ||
| 132 | (2007-2011). The data were collected by traffic police and completed | 132 | (2007-2011). The data were collected by traffic police and completed | ||
| 133 | with data provided by road management teams, the traffic management | 133 | with data provided by road management teams, the traffic management | ||
| 134 | agency and the wildlife management department. Two different methods | 134 | agency and the wildlife management department. Two different methods | ||
| 135 | were used to determine the location of the clusters of accidents | 135 | were used to determine the location of the clusters of accidents | ||
| 136 | caused by ungulates. First the kernel density estimation (KDE) was | 136 | caused by ungulates. First the kernel density estimation (KDE) was | ||
| 137 | applied to the 1-km stretches of road that had previously been | 137 | applied to the 1-km stretches of road that had previously been | ||
| 138 | identified as the most conflictive by comparing the data with a random | 138 | identified as the most conflictive by comparing the data with a random | ||
| 139 | situation in which the probability of occurrence along each stretch | 139 | situation in which the probability of occurrence along each stretch | ||
| 140 | followed a Poisson distribution. However, this method could not be | 140 | followed a Poisson distribution. However, this method could not be | ||
| 141 | used to determine the statistical significance of the clusters that | 141 | used to determine the statistical significance of the clusters that | ||
| 142 | were identified. The second method (KDE+) consisted of a procedure | 142 | were identified. The second method (KDE+) consisted of a procedure | ||
| 143 | based on standard KDE that identify the most hazardous road stretches | 143 | based on standard KDE that identify the most hazardous road stretches | ||
| 144 | by testing the statistical significance of the resulting clusters. The | 144 | by testing the statistical significance of the resulting clusters. The | ||
| 145 | clusters were identified where the kernel density function exceeded | 145 | clusters were identified where the kernel density function exceeded | ||
| 146 | the significance level corresponding to the 95th percentile, and the | 146 | the significance level corresponding to the 95th percentile, and the | ||
| 147 | application of cluster strength evaluation provided a sorted list of | 147 | application of cluster strength evaluation provided a sorted list of | ||
| 148 | hazardous locations. Traffic accidents caused by ungulates mainly | 148 | hazardous locations. Traffic accidents caused by ungulates mainly | ||
| 149 | wild boar and deer) have a strong tendency to cluster, with about one | 149 | wild boar and deer) have a strong tendency to cluster, with about one | ||
| 150 | third of accidents located at around 1% of the road network length. | 150 | third of accidents located at around 1% of the road network length. | ||
| 151 | The results provided by this method allow efforts to apply mitigation | 151 | The results provided by this method allow efforts to apply mitigation | ||
| 152 | measures to be focused on the most hazardous road stretches, where the | 152 | measures to be focused on the most hazardous road stretches, where the | ||
| 153 | best benefit-cost ratio can be expected.", | 153 | best benefit-cost ratio can be expected.", | ||
| 154 | "es": "Animal Vehicle Collisions (AVC) often show a pattern of | 154 | "es": "Animal Vehicle Collisions (AVC) often show a pattern of | ||
| 155 | aggregation, with clusters along conflictive road stretches. Road | 155 | aggregation, with clusters along conflictive road stretches. Road | ||
| 156 | traffic safety is diminished in these hotspots, due to the risk of | 156 | traffic safety is diminished in these hotspots, due to the risk of | ||
| 157 | accidents involving animals. Therefore, the identification of these | 157 | accidents involving animals. Therefore, the identification of these | ||
| 158 | stretches is essential to apply effective mitigation measures. Data | 158 | stretches is essential to apply effective mitigation measures. Data | ||
| 159 | from 2,110 accidents involving ungulates were registered in the 12,124 | 159 | from 2,110 accidents involving ungulates were registered in the 12,124 | ||
| 160 | km of the Catalan (NE Spain) road network during a five-year period | 160 | km of the Catalan (NE Spain) road network during a five-year period | ||
| 161 | (2007-2011). The data were collected by traffic police and completed | 161 | (2007-2011). The data were collected by traffic police and completed | ||
| 162 | with data provided by road management teams, the traffic management | 162 | with data provided by road management teams, the traffic management | ||
| 163 | agency and the wildlife management department. Two different methods | 163 | agency and the wildlife management department. Two different methods | ||
| 164 | were used to determine the location of the clusters of accidents | 164 | were used to determine the location of the clusters of accidents | ||
| 165 | caused by ungulates. First the kernel density estimation (KDE) was | 165 | caused by ungulates. First the kernel density estimation (KDE) was | ||
| 166 | applied to the 1-km stretches of road that had previously been | 166 | applied to the 1-km stretches of road that had previously been | ||
| 167 | identified as the most conflictive by comparing the data with a random | 167 | identified as the most conflictive by comparing the data with a random | ||
| 168 | situation in which the probability of occurrence along each stretch | 168 | situation in which the probability of occurrence along each stretch | ||
| 169 | followed a Poisson distribution. However, this method could not be | 169 | followed a Poisson distribution. However, this method could not be | ||
| 170 | used to determine the statistical significance of the clusters that | 170 | used to determine the statistical significance of the clusters that | ||
| 171 | were identified. The second method (KDE+) consisted of a procedure | 171 | were identified. The second method (KDE+) consisted of a procedure | ||
| 172 | based on standard KDE that identify the most hazardous road stretches | 172 | based on standard KDE that identify the most hazardous road stretches | ||
| 173 | by testing the statistical significance of the resulting clusters. The | 173 | by testing the statistical significance of the resulting clusters. The | ||
| 174 | clusters were identified where the kernel density function exceeded | 174 | clusters were identified where the kernel density function exceeded | ||
| 175 | the significance level corresponding to the 95th percentile, and the | 175 | the significance level corresponding to the 95th percentile, and the | ||
| 176 | application of cluster strength evaluation provided a sorted list of | 176 | application of cluster strength evaluation provided a sorted list of | ||
| 177 | hazardous locations. Traffic accidents caused by ungulates mainly wild | 177 | hazardous locations. Traffic accidents caused by ungulates mainly wild | ||
| 178 | boar and deer) have a strong tendency to cluster, with about one third | 178 | boar and deer) have a strong tendency to cluster, with about one third | ||
| 179 | of accidents located at around 1% of the road network length. The | 179 | of accidents located at around 1% of the road network length. The | ||
| 180 | results provided by this method allow efforts to apply mitigation | 180 | results provided by this method allow efforts to apply mitigation | ||
| 181 | measures to be focused on the most hazardous road stretches, where the | 181 | measures to be focused on the most hazardous road stretches, where the | ||
| 182 | best benefit-cost ratio can be expected." | 182 | best benefit-cost ratio can be expected." | ||
| 183 | }, | 183 | }, | ||
| 184 | "num_resources": 1, | 184 | "num_resources": 1, | ||
| 185 | "num_tags": 2, | 185 | "num_tags": 2, | ||
| 186 | "organization": { | 186 | "organization": { | ||
| 187 | "approval_status": "approved", | 187 | "approval_status": "approved", | ||
| 188 | "created": "2026-06-23T14:36:08.942021", | 188 | "created": "2026-06-23T14:36:08.942021", | ||
| 189 | "description": "", | 189 | "description": "", | ||
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| 191 | "image_url": "", | 191 | "image_url": "", | ||
| 192 | "is_organization": true, | 192 | "is_organization": true, | ||
| 193 | "name": "iepnb", | 193 | "name": "iepnb", | ||
| 194 | "state": "active", | 194 | "state": "active", | ||
| 195 | "title": "", | 195 | "title": "", | ||
| 196 | "type": "organization" | 196 | "type": "organization" | ||
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| 206 | "email": "buzon-bdatos@miteco.es", | 206 | "email": "buzon-bdatos@miteco.es", | ||
| 207 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 207 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 208 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 208 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 209 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 209 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 210 | Demogr\u00e1fico", | 210 | Demogr\u00e1fico", | ||
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| 212 | "uri": "https://iepnb.es/catalogo/organization/iepnb", | 212 | "uri": "https://iepnb.es/catalogo/organization/iepnb", | ||
| 213 | "url": "https://www.miteco.gob.es/" | 213 | "url": "https://www.miteco.gob.es/" | ||
| 214 | } | 214 | } | ||
| 215 | ], | 215 | ], | ||
| 216 | "publisher_email": "buzon-bdatos@miteco.es", | 216 | "publisher_email": "buzon-bdatos@miteco.es", | ||
| 217 | "publisher_name": "\u00c1rea de Banco de Datos de la Naturaleza. | 217 | "publisher_name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 218 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 218 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 219 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 219 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 220 | Demogr\u00e1fico", | 220 | Demogr\u00e1fico", | ||
| 221 | "publisher_type": | 221 | "publisher_type": | ||
| 222 | "http://purl.org/adms/publishertype/NationalAuthority", | 222 | "http://purl.org/adms/publishertype/NationalAuthority", | ||
| 223 | "publisher_uri": "https://iepnb.es/catalogo/organization/iepnb", | 223 | "publisher_uri": "https://iepnb.es/catalogo/organization/iepnb", | ||
| 224 | "publisher_url": "https://www.miteco.gob.es/", | 224 | "publisher_url": "https://www.miteco.gob.es/", | ||
| 225 | "purpose": { | 225 | "purpose": { | ||
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| 229 | "reference": [], | 229 | "reference": [], | ||
| 230 | "relationships_as_object": [], | 230 | "relationships_as_object": [], | ||
| 231 | "relationships_as_subject": [], | 231 | "relationships_as_subject": [], | ||
| 232 | "resources": [ | 232 | "resources": [ | ||
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