Cambios
En el instante 23 de junio de 2026, 15:59:02 UTC,
-
Modificado el valor del campo
spatial_coverage
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en Mitigation of barrier effect of linear infrastructures on wildlife.
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| 4 | "alternate_identifier": "ISBN: 90-369-3727-2", | 4 | "alternate_identifier": "ISBN: 90-369-3727-2", | ||
| 5 | "author": "Rosell, C., Parpal, J., Campeny, R., Jov\u00e9, S., | 5 | "author": "Rosell, C., Parpal, J., Campeny, R., Jov\u00e9, S., | ||
| 6 | Pasquina, A. y Velasco, J.M.", | 6 | Pasquina, A. y Velasco, J.M.", | ||
| 7 | "author_name": "Rosell, C., Parpal, J., Campeny, R., Jov\u00e9, S., | 7 | "author_name": "Rosell, C., Parpal, J., Campeny, R., Jov\u00e9, S., | ||
| 8 | Pasquina, A. y Velasco, J.M.", | 8 | Pasquina, A. y Velasco, J.M.", | ||
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| 33 | "created": "2025-05-23", | 33 | "created": "2025-05-23", | ||
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| 36 | "name": "Rosell, C., Parpal, J., Campeny, R., Jov\u00e9, S., | 36 | "name": "Rosell, C., Parpal, J., Campeny, R., Jov\u00e9, S., | ||
| 37 | Pasquina, A. y Velasco, J.M." | 37 | Pasquina, A. y Velasco, J.M." | ||
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| 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", | ||
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| 50 | "identifier": "d1081d7a-4d94-56f2-8b55-b4bf78ac9043", | 50 | "identifier": "d1081d7a-4d94-56f2-8b55-b4bf78ac9043", | ||
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| 55 | "license_id": "cc-by", | 55 | "license_id": "cc-by", | ||
| 56 | "license_title": "Creative Commons Attribution", | 56 | "license_title": "Creative Commons Attribution", | ||
| 57 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 57 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
| 58 | "lineage_process_steps": [], | 58 | "lineage_process_steps": [], | ||
| 59 | "lineage_source": [ | 59 | "lineage_source": [ | ||
| 60 | "Habitat fragmentation and infrastructure", | 60 | "Habitat fragmentation and infrastructure", | ||
| 61 | "pags. 367-372" | 61 | "pags. 367-372" | ||
| 62 | ], | 62 | ], | ||
| 63 | "maintainer": "", | 63 | "maintainer": "", | ||
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| 65 | "metadata_created": "2026-06-23T14:49:19.664703", | 65 | "metadata_created": "2026-06-23T14:49:19.664703", | ||
| n | 66 | "metadata_modified": "2026-06-23T14:49:19.664708", | n | 66 | "metadata_modified": "2026-06-23T15:59:02.211976", |
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| 70 | "miteco_data_population": { | 70 | "miteco_data_population": { | ||
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| 73 | "miteco_data_territory": { | 73 | "miteco_data_territory": { | ||
| 74 | "es": "" | 74 | "es": "" | ||
| 75 | }, | 75 | }, | ||
| 76 | "miteco_dataset_type": | 76 | "miteco_dataset_type": | ||
| 77 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 77 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 78 | "miteco_geo_level": "1", | 78 | "miteco_geo_level": "1", | ||
| 79 | "modified": "2026-06-23", | 79 | "modified": "2026-06-23", | ||
| 80 | "name": "d1081d7a-4d94-56f2-8b55-b4bf78ac9043", | 80 | "name": "d1081d7a-4d94-56f2-8b55-b4bf78ac9043", | ||
| 81 | "notes": "The permeabilisation of linear infrastructures is | 81 | "notes": "The permeabilisation of linear infrastructures is | ||
| 82 | essential to mitigate the fragmentation that new infrastructures cause | 82 | essential to mitigate the fragmentation that new infrastructures cause | ||
| 83 | on wildlife populations. Although in some locations specific wildlife | 83 | on wildlife populations. Although in some locations specific wildlife | ||
| 84 | passages can be constructed, usually drains are conditioned for use by | 84 | passages can be constructed, usually drains are conditioned for use by | ||
| 85 | fauna. A study was carried out in Catalonia (NE Spain) to identify the | 85 | fauna. A study was carried out in Catalonia (NE Spain) to identify the | ||
| 86 | structural and environmental characteristics that have a significant | 86 | structural and environmental characteristics that have a significant | ||
| 87 | influence on the use of a transversal structure as a wildlife passage. | 87 | influence on the use of a transversal structure as a wildlife passage. | ||
| 88 | 56 transversal structures (potentially useful wildlife passages) were | 88 | 56 transversal structures (potentially useful wildlife passages) were | ||
| 89 | checked to determine their use; 39 were circular cross-section (from 1 | 89 | checked to determine their use; 39 were circular cross-section (from 1 | ||
| 90 | to 3 m diameter) and 17 were rectangular cross-section (from 4 to 12 m | 90 | to 3 m diameter) and 17 were rectangular cross-section (from 4 to 12 m | ||
| 91 | wide) . Information was obtained by registering animal tracks on a | 91 | wide) . Information was obtained by registering animal tracks on a | ||
| 92 | marble powder bed and by using infra-red film cameras and photographic | 92 | marble powder bed and by using infra-red film cameras and photographic | ||
| 93 | cameras. The preferences of the different taxonomic groups have been | 93 | cameras. The preferences of the different taxonomic groups have been | ||
| 94 | analyzed to facilitate the design of projects to condition transversal | 94 | analyzed to facilitate the design of projects to condition transversal | ||
| 95 | structures as wildlife passages. These preferences were shown to be | 95 | structures as wildlife passages. These preferences were shown to be | ||
| 96 | remarkably different for each group. Small mammals and carnivores were | 96 | remarkably different for each group. Small mammals and carnivores were | ||
| 97 | the groups which were detected more frequently using the monitored | 97 | the groups which were detected more frequently using the monitored | ||
| 98 | structures. Ungulates present on the area (roe deer and wild boar) do | 98 | structures. Ungulates present on the area (roe deer and wild boar) do | ||
| 99 | not use the structures during the monitoring period. A specific survey | 99 | not use the structures during the monitoring period. A specific survey | ||
| 100 | cheking once a month the underpasses during one year established that | 100 | cheking once a month the underpasses during one year established that | ||
| 101 | wild boar used (but only ocasionally) structures more than 7 m wide.\n | 101 | wild boar used (but only ocasionally) structures more than 7 m wide.\n | ||
| 102 | Palabras clave: Barrier, Culvert, Drainage, Effectiveness, Fauna | 102 | Palabras clave: Barrier, Culvert, Drainage, Effectiveness, Fauna | ||
| 103 | passage, Monitoring, Overpass, Underpass, Vertebrate, Wildlife | 103 | passage, Monitoring, Overpass, Underpass, Vertebrate, Wildlife | ||
| 104 | passage", | 104 | passage", | ||
| 105 | "notes_translated": { | 105 | "notes_translated": { | ||
| 106 | "en": "The permeabilisation of linear infrastructures is essential | 106 | "en": "The permeabilisation of linear infrastructures is essential | ||
| 107 | to mitigate the fragmentation that new infrastructures cause on | 107 | to mitigate the fragmentation that new infrastructures cause on | ||
| 108 | wildlife populations. Although in some locations specific wildlife | 108 | wildlife populations. Although in some locations specific wildlife | ||
| 109 | passages can be constructed, usually drains are conditioned for use by | 109 | passages can be constructed, usually drains are conditioned for use by | ||
| 110 | fauna. A study was carried out in Catalonia (NE Spain) to identify the | 110 | fauna. A study was carried out in Catalonia (NE Spain) to identify the | ||
| 111 | structural and environmental characteristics that have a significant | 111 | structural and environmental characteristics that have a significant | ||
| 112 | influence on the use of a transversal structure as a wildlife passage. | 112 | influence on the use of a transversal structure as a wildlife passage. | ||
| 113 | 56 transversal structures (potentially useful wildlife passages) were | 113 | 56 transversal structures (potentially useful wildlife passages) were | ||
| 114 | checked to determine their use; 39 were circular cross-section (from 1 | 114 | checked to determine their use; 39 were circular cross-section (from 1 | ||
| 115 | to 3 m diameter) and 17 were rectangular cross-section (from 4 to 12 m | 115 | to 3 m diameter) and 17 were rectangular cross-section (from 4 to 12 m | ||
| 116 | wide) . Information was obtained by registering animal tracks on a | 116 | wide) . Information was obtained by registering animal tracks on a | ||
| 117 | marble powder bed and by using infra-red film cameras and photographic | 117 | marble powder bed and by using infra-red film cameras and photographic | ||
| 118 | cameras. The preferences of the different taxonomic groups have been | 118 | cameras. The preferences of the different taxonomic groups have been | ||
| 119 | analyzed to facilitate the design of projects to condition transversal | 119 | analyzed to facilitate the design of projects to condition transversal | ||
| 120 | structures as wildlife passages. These preferences were shown to be | 120 | structures as wildlife passages. These preferences were shown to be | ||
| 121 | remarkably different for each group. Small mammals and carnivores were | 121 | remarkably different for each group. Small mammals and carnivores were | ||
| 122 | the groups which were detected more frequently using the monitored | 122 | the groups which were detected more frequently using the monitored | ||
| 123 | structures. Ungulates present on the area (roe deer and wild boar) do | 123 | structures. Ungulates present on the area (roe deer and wild boar) do | ||
| 124 | not use the structures during the monitoring period. A specific survey | 124 | not use the structures during the monitoring period. A specific survey | ||
| 125 | cheking once a month the underpasses during one year established that | 125 | cheking once a month the underpasses during one year established that | ||
| 126 | wild boar used (but only ocasionally) structures more than 7 m | 126 | wild boar used (but only ocasionally) structures more than 7 m | ||
| 127 | wide.\n\n\nLa permeabilizaci\u00f3n de infraestructuras lineales es | 127 | wide.\n\n\nLa permeabilizaci\u00f3n de infraestructuras lineales es | ||
| 128 | esencial para mitigar la fragmentaci\u00f3n que las nuevas v\u00edas | 128 | esencial para mitigar la fragmentaci\u00f3n que las nuevas v\u00edas | ||
| 129 | pueden causar en las poblaciones animales. Aunque en algunas | 129 | pueden causar en las poblaciones animales. Aunque en algunas | ||
| 130 | infraestructuras pueden construirse pasos espec\u00edficos para la | 130 | infraestructuras pueden construirse pasos espec\u00edficos para la | ||
| 131 | fauna, normalmente se adaptan drenajes y pasos inferiores para que | 131 | fauna, normalmente se adaptan drenajes y pasos inferiores para que | ||
| 132 | puedan ser utilizados tambi\u00e9n por la fauna. En Catalunya (NE de | 132 | puedan ser utilizados tambi\u00e9n por la fauna. En Catalunya (NE de | ||
| 133 | Espa\u00f1a) se llev\u00f3 a cabo un estudio con el objetivo de | 133 | Espa\u00f1a) se llev\u00f3 a cabo un estudio con el objetivo de | ||
| 134 | identificar las caracter\u00edsticas ambientales y estructurales que | 134 | identificar las caracter\u00edsticas ambientales y estructurales que | ||
| 135 | tienen una influencia significativa en el paso de fauna. 56 | 135 | tienen una influencia significativa en el paso de fauna. 56 | ||
| 136 | estructuras transversales (potencialmente utilitzables como pasos de | 136 | estructuras transversales (potencialmente utilitzables como pasos de | ||
| 137 | fauna) se controlaron para determinar si eran utilizadas o no por los | 137 | fauna) se controlaron para determinar si eran utilizadas o no por los | ||
| 138 | animales; 39 eran de secci\u00f3n circular (de 1 a 3 m de | 138 | animales; 39 eran de secci\u00f3n circular (de 1 a 3 m de | ||
| 139 | di\u00e1metro) y 17 eran de secci\u00f3n rectangular (de 4 a 12 m de | 139 | di\u00e1metro) y 17 eran de secci\u00f3n rectangular (de 4 a 12 m de | ||
| 140 | ancho). La informaci\u00f3n se obtuvo registrando huellas sobre un | 140 | ancho). La informaci\u00f3n se obtuvo registrando huellas sobre un | ||
| 141 | sustrato de polvo de m\u00e1rmol y utilizando camaras de | 141 | sustrato de polvo de m\u00e1rmol y utilizando camaras de | ||
| 142 | filmaci\u00f3n y fotogr\u00e1ficas activadas por un haz de | 142 | filmaci\u00f3n y fotogr\u00e1ficas activadas por un haz de | ||
| 143 | infrarrojos. Las preferencias de los distintos grupos taxon\u00f3micos | 143 | infrarrojos. Las preferencias de los distintos grupos taxon\u00f3micos | ||
| 144 | fueron analizadas para facilitar recomendaciones aplicables al | 144 | fueron analizadas para facilitar recomendaciones aplicables al | ||
| 145 | acondicionamiento de estructuras transversales como pasos de fauna. | 145 | acondicionamiento de estructuras transversales como pasos de fauna. | ||
| 146 | Las caracter\u00edsticas que facilitan el paso de fauna mostraron | 146 | Las caracter\u00edsticas que facilitan el paso de fauna mostraron | ||
| 147 | notables diferencias para cada uno de los grupos analizados. Los | 147 | notables diferencias para cada uno de los grupos analizados. Los | ||
| 148 | peque\u00f1os mam\u00edferos y los carn\u00edvorsos fueron los grupos | 148 | peque\u00f1os mam\u00edferos y los carn\u00edvorsos fueron los grupos | ||
| 149 | que se detectaron con mayor frecuencia. Los ungulados presentes en el | 149 | que se detectaron con mayor frecuencia. Los ungulados presentes en el | ||
| 150 | \u00e1rea (corzo y jabal\u00ed) no utilizaron ninguna de las | 150 | \u00e1rea (corzo y jabal\u00ed) no utilizaron ninguna de las | ||
| 151 | estructuras durante el per\u00edodo de muestreo. Una prospecci\u00f3n | 151 | estructuras durante el per\u00edodo de muestreo. Una prospecci\u00f3n | ||
| 152 | espec\u00edfica que se llev\u00f3 a cabo en los pasos inferiores una | 152 | espec\u00edfica que se llev\u00f3 a cabo en los pasos inferiores una | ||
| 153 | vez al mes durante un a\u00f1o, estableci\u00f3 que el jabal\u00ed | 153 | vez al mes durante un a\u00f1o, estableci\u00f3 que el jabal\u00ed | ||
| 154 | utilizaba (aunque s\u00f3lo ocasionalmente) las estructuras de | 154 | utilizaba (aunque s\u00f3lo ocasionalmente) las estructuras de | ||
| 155 | m\u00e1s de 7 m de anchura.", | 155 | m\u00e1s de 7 m de anchura.", | ||
| 156 | "es": "The permeabilisation of linear infrastructures is essential | 156 | "es": "The permeabilisation of linear infrastructures is essential | ||
| 157 | to mitigate the fragmentation that new infrastructures cause on | 157 | to mitigate the fragmentation that new infrastructures cause on | ||
| 158 | wildlife populations. Although in some locations specific wildlife | 158 | wildlife populations. Although in some locations specific wildlife | ||
| 159 | passages can be constructed, usually drains are conditioned for use by | 159 | passages can be constructed, usually drains are conditioned for use by | ||
| 160 | fauna. A study was carried out in Catalonia (NE Spain) to identify the | 160 | fauna. A study was carried out in Catalonia (NE Spain) to identify the | ||
| 161 | structural and environmental characteristics that have a significant | 161 | structural and environmental characteristics that have a significant | ||
| 162 | influence on the use of a transversal structure as a wildlife passage. | 162 | influence on the use of a transversal structure as a wildlife passage. | ||
| 163 | 56 transversal structures (potentially useful wildlife passages) were | 163 | 56 transversal structures (potentially useful wildlife passages) were | ||
| 164 | checked to determine their use; 39 were circular cross-section (from 1 | 164 | checked to determine their use; 39 were circular cross-section (from 1 | ||
| 165 | to 3 m diameter) and 17 were rectangular cross-section (from 4 to 12 m | 165 | to 3 m diameter) and 17 were rectangular cross-section (from 4 to 12 m | ||
| 166 | wide) . Information was obtained by registering animal tracks on a | 166 | wide) . Information was obtained by registering animal tracks on a | ||
| 167 | marble powder bed and by using infra-red film cameras and photographic | 167 | marble powder bed and by using infra-red film cameras and photographic | ||
| 168 | cameras. The preferences of the different taxonomic groups have been | 168 | cameras. The preferences of the different taxonomic groups have been | ||
| 169 | analyzed to facilitate the design of projects to condition transversal | 169 | analyzed to facilitate the design of projects to condition transversal | ||
| 170 | structures as wildlife passages. These preferences were shown to be | 170 | structures as wildlife passages. These preferences were shown to be | ||
| 171 | remarkably different for each group. Small mammals and carnivores were | 171 | remarkably different for each group. Small mammals and carnivores were | ||
| 172 | the groups which were detected more frequently using the monitored | 172 | the groups which were detected more frequently using the monitored | ||
| 173 | structures. Ungulates present on the area (roe deer and wild boar) do | 173 | structures. Ungulates present on the area (roe deer and wild boar) do | ||
| 174 | not use the structures during the monitoring period. A specific survey | 174 | not use the structures during the monitoring period. A specific survey | ||
| 175 | cheking once a month the underpasses during one year established that | 175 | cheking once a month the underpasses during one year established that | ||
| 176 | wild boar used (but only ocasionally) structures more than 7 m wide.\n | 176 | wild boar used (but only ocasionally) structures more than 7 m wide.\n | ||
| 177 | Palabras clave: Barrier, Culvert, Drainage, Effectiveness, Fauna | 177 | Palabras clave: Barrier, Culvert, Drainage, Effectiveness, Fauna | ||
| 178 | passage, Monitoring, Overpass, Underpass, Vertebrate, Wildlife | 178 | passage, Monitoring, Overpass, Underpass, Vertebrate, Wildlife | ||
| 179 | passage" | 179 | passage" | ||
| 180 | }, | 180 | }, | ||
| 181 | "num_resources": 1, | 181 | "num_resources": 1, | ||
| 182 | "num_tags": 12, | 182 | "num_tags": 12, | ||
| 183 | "organization": { | 183 | "organization": { | ||
| 184 | "approval_status": "approved", | 184 | "approval_status": "approved", | ||
| 185 | "created": "2026-06-23T14:36:08.942021", | 185 | "created": "2026-06-23T14:36:08.942021", | ||
| 186 | "description": "", | 186 | "description": "", | ||
| 187 | "id": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | 187 | "id": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | ||
| 188 | "image_url": "", | 188 | "image_url": "", | ||
| 189 | "is_organization": true, | 189 | "is_organization": true, | ||
| 190 | "name": "iepnb", | 190 | "name": "iepnb", | ||
| 191 | "state": "active", | 191 | "state": "active", | ||
| 192 | "title": "", | 192 | "title": "", | ||
| 193 | "type": "organization" | 193 | "type": "organization" | ||
| 194 | }, | 194 | }, | ||
| 195 | "owner_org": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | 195 | "owner_org": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | ||
| 196 | "private": false, | 196 | "private": false, | ||
| 197 | "provenance": { | 197 | "provenance": { | ||
| 198 | "en": "", | 198 | "en": "", | ||
| 199 | "es": "" | 199 | "es": "" | ||
| 200 | }, | 200 | }, | ||
| 201 | "publisher": [ | 201 | "publisher": [ | ||
| 202 | { | 202 | { | ||
| 203 | "email": "buzon-bdatos@miteco.es", | 203 | "email": "buzon-bdatos@miteco.es", | ||
| 204 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 204 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 205 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 205 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 206 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 206 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 207 | Demogr\u00e1fico", | 207 | Demogr\u00e1fico", | ||
| 208 | "type": "http://purl.org/adms/publishertype/NationalAuthority", | 208 | "type": "http://purl.org/adms/publishertype/NationalAuthority", | ||
| 209 | "uri": "https://iepnb.es/catalogo/organization/iepnb", | 209 | "uri": "https://iepnb.es/catalogo/organization/iepnb", | ||
| 210 | "url": "https://www.miteco.gob.es/" | 210 | "url": "https://www.miteco.gob.es/" | ||
| 211 | } | 211 | } | ||
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