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) en Vertebrate ticks distribution and their role as vectors in relation to road edges and underpasses.
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| 79 | "notes": "Roads fragment vertebrate populations and affect the | 93 | "notes": "Roads fragment vertebrate populations and affect the | ||
| 80 | dynamics and dispersal patterns of vertebrate parasites. We evaluated | 94 | dynamics and dispersal patterns of vertebrate parasites. We evaluated | ||
| 81 | how vertebrate ticks distribute near roads and road underpasses in | 95 | how vertebrate ticks distribute near roads and road underpasses in | ||
| 82 | human-caused road-fragmented landscapes in Seville, SW Spain. We | 96 | human-caused road-fragmented landscapes in Seville, SW Spain. We | ||
| 83 | sampled 49 stations with 93 individualized sampling points and | 97 | sampled 49 stations with 93 individualized sampling points and | ||
| 84 | assessed tick abundance. We explored the relationship between tick | 98 | assessed tick abundance. We explored the relationship between tick | ||
| 85 | presence and abundance and distance to the nearest road and underpass | 99 | presence and abundance and distance to the nearest road and underpass | ||
| 86 | (drainage culverts and other passages used by vertebrates), and | 100 | (drainage culverts and other passages used by vertebrates), and | ||
| 87 | landscape features through categorical regression and nonparametric | 101 | landscape features through categorical regression and nonparametric | ||
| 88 | statistics. The presence of the tick-borne pathogens Borrelia sp. and | 102 | statistics. The presence of the tick-borne pathogens Borrelia sp. and | ||
| 89 | Bartonella sp. was also analyzed by PCR. We found preliminary evidence | 103 | Bartonella sp. was also analyzed by PCR. We found preliminary evidence | ||
| 90 | of high relative tick abundance next to roads and in the vicinity of | 104 | of high relative tick abundance next to roads and in the vicinity of | ||
| 91 | road underpasses. Plant cover type was related to tick presence in | 105 | road underpasses. Plant cover type was related to tick presence in | ||
| 92 | this road context. Implications of road permeability and edge effect | 106 | this road context. Implications of road permeability and edge effect | ||
| 93 | in patterns of vertebrate\u2013tick relationships in road | 107 | in patterns of vertebrate\u2013tick relationships in road | ||
| 94 | fragmentation contexts are discussed. Both Borrelia sp. and Bartonella | 108 | fragmentation contexts are discussed. Both Borrelia sp. and Bartonella | ||
| 95 | sp. were detected in the ticks analyzed. This is the first report of | 109 | sp. were detected in the ticks analyzed. This is the first report of | ||
| 96 | these bacteria in ticks from Seville. The results confirm the | 110 | these bacteria in ticks from Seville. The results confirm the | ||
| 97 | potential risk of acquiring Lyme disease and bartonellosis in this | 111 | potential risk of acquiring Lyme disease and bartonellosis in this | ||
| 98 | area.", | 112 | area.", | ||
| 99 | "notes_translated": { | 113 | "notes_translated": { | ||
| 100 | "en": "Roads fragment vertebrate populations and affect the | 114 | "en": "Roads fragment vertebrate populations and affect the | ||
| 101 | dynamics and dispersal patterns of vertebrate parasites. We evaluated | 115 | dynamics and dispersal patterns of vertebrate parasites. We evaluated | ||
| 102 | how vertebrate ticks distribute near roads and road underpasses in | 116 | how vertebrate ticks distribute near roads and road underpasses in | ||
| 103 | human-caused road-fragmented landscapes in Seville, SW Spain. We | 117 | human-caused road-fragmented landscapes in Seville, SW Spain. We | ||
| 104 | sampled 49 stations with 93 individualized sampling points and | 118 | sampled 49 stations with 93 individualized sampling points and | ||
| 105 | assessed tick abundance. We explored the relationship between tick | 119 | assessed tick abundance. We explored the relationship between tick | ||
| 106 | presence and abundance and distance to the nearest road and underpass | 120 | presence and abundance and distance to the nearest road and underpass | ||
| 107 | (drainage culverts and other passages used by vertebrates), and | 121 | (drainage culverts and other passages used by vertebrates), and | ||
| 108 | landscape features through categorical regression and nonparametric | 122 | landscape features through categorical regression and nonparametric | ||
| 109 | statistics. The presence of the tick-borne pathogens Borrelia sp. and | 123 | statistics. The presence of the tick-borne pathogens Borrelia sp. and | ||
| 110 | Bartonella sp. was also analyzed by PCR. We found preliminary evidence | 124 | Bartonella sp. was also analyzed by PCR. We found preliminary evidence | ||
| 111 | of high relative tick abundance next to roads and in the vicinity of | 125 | of high relative tick abundance next to roads and in the vicinity of | ||
| 112 | road underpasses. Plant cover type was related to tick presence in | 126 | road underpasses. Plant cover type was related to tick presence in | ||
| 113 | this road context. Implications of road permeability and edge effect | 127 | this road context. Implications of road permeability and edge effect | ||
| 114 | in patterns of vertebrate\u2013tick relationships in road | 128 | in patterns of vertebrate\u2013tick relationships in road | ||
| 115 | fragmentation contexts are discussed. Both Borrelia sp. and Bartonella | 129 | fragmentation contexts are discussed. Both Borrelia sp. and Bartonella | ||
| 116 | sp. were detected in the ticks analyzed. This is the first report of | 130 | sp. were detected in the ticks analyzed. This is the first report of | ||
| 117 | these bacteria in ticks from Seville. The results confirm the | 131 | these bacteria in ticks from Seville. The results confirm the | ||
| 118 | potential risk of acquiring Lyme disease and bartonellosis in this | 132 | potential risk of acquiring Lyme disease and bartonellosis in this | ||
| 119 | area.", | 133 | area.", | ||
| 120 | "es": "Roads fragment vertebrate populations and affect the | 134 | "es": "Roads fragment vertebrate populations and affect the | ||
| 121 | dynamics and dispersal patterns of vertebrate parasites. We evaluated | 135 | dynamics and dispersal patterns of vertebrate parasites. We evaluated | ||
| 122 | how vertebrate ticks distribute near roads and road underpasses in | 136 | how vertebrate ticks distribute near roads and road underpasses in | ||
| 123 | human-caused road-fragmented landscapes in Seville, SW Spain. We | 137 | human-caused road-fragmented landscapes in Seville, SW Spain. We | ||
| 124 | sampled 49 stations with 93 individualized sampling points and | 138 | sampled 49 stations with 93 individualized sampling points and | ||
| 125 | assessed tick abundance. We explored the relationship between tick | 139 | assessed tick abundance. We explored the relationship between tick | ||
| 126 | presence and abundance and distance to the nearest road and underpass | 140 | presence and abundance and distance to the nearest road and underpass | ||
| 127 | (drainage culverts and other passages used by vertebrates), and | 141 | (drainage culverts and other passages used by vertebrates), and | ||
| 128 | landscape features through categorical regression and nonparametric | 142 | landscape features through categorical regression and nonparametric | ||
| 129 | statistics. The presence of the tick-borne pathogens Borrelia sp. and | 143 | statistics. The presence of the tick-borne pathogens Borrelia sp. and | ||
| 130 | Bartonella sp. was also analyzed by PCR. We found preliminary evidence | 144 | Bartonella sp. was also analyzed by PCR. We found preliminary evidence | ||
| 131 | of high relative tick abundance next to roads and in the vicinity of | 145 | of high relative tick abundance next to roads and in the vicinity of | ||
| 132 | road underpasses. Plant cover type was related to tick presence in | 146 | road underpasses. Plant cover type was related to tick presence in | ||
| 133 | this road context. Implications of road permeability and edge effect | 147 | this road context. Implications of road permeability and edge effect | ||
| 134 | in patterns of vertebrate\u2013tick relationships in road | 148 | in patterns of vertebrate\u2013tick relationships in road | ||
| 135 | fragmentation contexts are discussed. Both Borrelia sp. and Bartonella | 149 | fragmentation contexts are discussed. Both Borrelia sp. and Bartonella | ||
| 136 | sp. were detected in the ticks analyzed. This is the first report of | 150 | sp. were detected in the ticks analyzed. This is the first report of | ||
| 137 | these bacteria in ticks from Seville. The results confirm the | 151 | these bacteria in ticks from Seville. The results confirm the | ||
| 138 | potential risk of acquiring Lyme disease and bartonellosis in this | 152 | potential risk of acquiring Lyme disease and bartonellosis in this | ||
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| 237 | 27.64]]]}", | 251 | 27.64]]]}", | ||
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| 246 | "uri": | 260 | "uri": | ||
| 247 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 261 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
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| 251 | "spatial_uri": | 265 | "spatial_uri": | ||
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| 253 | "state": "active", | 267 | "state": "active", | ||
| 254 | "study_variables": { | 268 | "study_variables": { | ||
| 255 | "es": "" | 269 | "es": "" | ||
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| 257 | "tag_uri": [ | 271 | "tag_uri": [ | ||
| 258 | 272 | ||||
| 259 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 273 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 260 | ], | 274 | ], | ||
| 261 | "tags": [ | 275 | "tags": [ | ||
| 262 | { | 276 | { | ||
| 263 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | 277 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 264 | "id": "2379c860-0540-450a-9a23-72454ee80469", | 278 | "id": "2379c860-0540-450a-9a23-72454ee80469", | ||
| 265 | "name": "aspectos-globales-sobre-fragmentacion-de", | 279 | "name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 266 | "state": "active", | 280 | "state": "active", | ||
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| 270 | "display_name": "fragmentacion", | 284 | "display_name": "fragmentacion", | ||
| 271 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 285 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 272 | "name": "fragmentacion", | 286 | "name": "fragmentacion", | ||
| 273 | "state": "active", | 287 | "state": "active", | ||
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| 275 | } | 289 | } | ||
| 276 | ], | 290 | ], | ||
| 277 | "thematic_area": [ | 291 | "thematic_area": [ | ||
| 278 | "especies_silvestres" | 292 | "especies_silvestres" | ||
| 279 | ], | 293 | ], | ||
| 280 | "theme_es": [ | 294 | "theme_es": [ | ||
| 281 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 295 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 282 | ], | 296 | ], | ||
| 283 | "title": "Vertebrate ticks distribution and their role as vectors in | 297 | "title": "Vertebrate ticks distribution and their role as vectors in | ||
| 284 | relation to road edges and underpasses.", | 298 | relation to road edges and underpasses.", | ||
| 285 | "title_translated": { | 299 | "title_translated": { | ||
| 286 | "en": "", | 300 | "en": "", | ||
| 287 | "es": "Vertebrate ticks distribution and their role as vectors in | 301 | "es": "Vertebrate ticks distribution and their role as vectors in | ||
| 288 | relation to road edges and underpasses." | 302 | relation to road edges and underpasses." | ||
| 289 | }, | 303 | }, | ||
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| 291 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 305 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 292 | "type": "dataset", | 306 | "type": "dataset", | ||
| 293 | "url": | 307 | "url": | ||
| 294 | //iepnb.es:443/catalogo/dataset/7704ddbc-4c08-590b-a285-b27d2121436a", | 308 | //iepnb.es:443/catalogo/dataset/7704ddbc-4c08-590b-a285-b27d2121436a", | ||
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| 298 | "es": "" | 312 | "es": "" | ||
| 299 | } | 313 | } | ||
| 300 | } | 314 | } |