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En el instante 23 de junio de 2026, 16:12:34 UTC,
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spatial_coverage
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en Is vertebrate mortality correlated to potential permeability by underpasses along low-traffic roads?
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| 84 | "notes": "Road permeability to animal movements depends among | 84 | "notes": "Road permeability to animal movements depends among | ||
| 85 | several factors on structures which, integrated in the road design, | 85 | several factors on structures which, integrated in the road design, | ||
| 86 | operate as safe conducts to mitigate vehicle collision and barrier | 86 | operate as safe conducts to mitigate vehicle collision and barrier | ||
| 87 | effects. There is abundant evidence that wildlife makes use of such | 87 | effects. There is abundant evidence that wildlife makes use of such | ||
| 88 | structures as safe passages to cross roads. We analyzed the spatial | 88 | structures as safe passages to cross roads. We analyzed the spatial | ||
| 89 | relationship between road drainage elements (N = 253; mostly culverts) | 89 | relationship between road drainage elements (N = 253; mostly culverts) | ||
| 90 | as potential faunal underpasses, and mortality due to vehicle | 90 | as potential faunal underpasses, and mortality due to vehicle | ||
| 91 | collisions in two seasons and on four relatively low-traffic roads | 91 | collisions in two seasons and on four relatively low-traffic roads | ||
| 92 | (<5000 cars/day) traversing oak rangelands of western Andalusia (S | 92 | (<5000 cars/day) traversing oak rangelands of western Andalusia (S | ||
| 93 | Spain). Focusing on amphibians, reptiles and mammals, we recorded and | 93 | Spain). Focusing on amphibians, reptiles and mammals, we recorded and | ||
| 94 | located casualties (N = 238 individuals, 35 species) along these | 94 | located casualties (N = 238 individuals, 35 species) along these | ||
| 95 | roads, identifying and characterizing all potential underpasses. | 95 | roads, identifying and characterizing all potential underpasses. | ||
| 96 | Overall frequencies of casualties and spatial distribution were highly | 96 | Overall frequencies of casualties and spatial distribution were highly | ||
| 97 | variable both within and among these roads. We obtained an estimation | 97 | variable both within and among these roads. We obtained an estimation | ||
| 98 | of potential permeability for the different roads. We detected, | 98 | of potential permeability for the different roads. We detected, | ||
| 99 | located and described a wide supply and a very variable pattern of | 99 | located and described a wide supply and a very variable pattern of | ||
| 100 | drainage culverts and other underpasses, with differences among roads | 100 | drainage culverts and other underpasses, with differences among roads | ||
| 101 | in passage attributes potentially affecting permeability for wildlife, | 101 | in passage attributes potentially affecting permeability for wildlife, | ||
| 102 | such as spatial arrangement, number, density (frequency or | 102 | such as spatial arrangement, number, density (frequency or | ||
| 103 | concentration of passages) and dimensions. We used Mantel tests to | 103 | concentration of passages) and dimensions. We used Mantel tests to | ||
| 104 | assess spatial congruence of passages and road-killed animals. We | 104 | assess spatial congruence of passages and road-killed animals. We | ||
| 105 | applied generalized linear mixed models fitted by maximum likelihood | 105 | applied generalized linear mixed models fitted by maximum likelihood | ||
| 106 | through Akaike Information Criterion to explain the variation in the | 106 | through Akaike Information Criterion to explain the variation in the | ||
| 107 | distance of the 238 casualties to the nearest underpasses, with road | 107 | distance of the 238 casualties to the nearest underpasses, with road | ||
| 108 | transect and season as random factors, and traffic intensity, speed | 108 | transect and season as random factors, and traffic intensity, speed | ||
| 109 | and vertebrate class as fixed effects. Both road-killed animals and | 109 | and vertebrate class as fixed effects. Both road-killed animals and | ||
| 110 | underpass distribution followed aggregated patterns, and casualties | 110 | underpass distribution followed aggregated patterns, and casualties | ||
| 111 | were not significantly related to underpasses along any of the 4 | 111 | were not significantly related to underpasses along any of the 4 | ||
| 112 | roads. There were no differences in distance of casualties to the | 112 | roads. There were no differences in distance of casualties to the | ||
| 113 | nearest underpass for the three vertebrate classes. Although existing | 113 | nearest underpass for the three vertebrate classes. Although existing | ||
| 114 | underpasses were abundant, we could not correlate potential | 114 | underpasses were abundant, we could not correlate potential | ||
| 115 | permeability with reduced mortality along these roads, and other | 115 | permeability with reduced mortality along these roads, and other | ||
| 116 | factors potentially affecting roadkill aggregations should be | 116 | factors potentially affecting roadkill aggregations should be | ||
| 117 | evaluated along with permeability assessment. Mitigation of | 117 | evaluated along with permeability assessment. Mitigation of | ||
| 118 | road-caused mortality can still be greatly improved for these roads, | 118 | road-caused mortality can still be greatly improved for these roads, | ||
| 119 | through measures of reconditioning and proper management of existing | 119 | through measures of reconditioning and proper management of existing | ||
| 120 | underpasses, aiming to maximize road permeability and reducing major | 120 | underpasses, aiming to maximize road permeability and reducing major | ||
| 121 | impacts upon animal populations of Andalusian rangelands.", | 121 | impacts upon animal populations of Andalusian rangelands.", | ||
| 122 | "notes_translated": { | 122 | "notes_translated": { | ||
| 123 | "en": "Road permeability to animal movements depends among several | 123 | "en": "Road permeability to animal movements depends among several | ||
| 124 | factors on structures which, integrated in the road design, operate as | 124 | factors on structures which, integrated in the road design, operate as | ||
| 125 | safe conducts to mitigate vehicle collision and barrier effects. There | 125 | safe conducts to mitigate vehicle collision and barrier effects. There | ||
| 126 | is abundant evidence that wildlife makes use of such structures as | 126 | is abundant evidence that wildlife makes use of such structures as | ||
| 127 | safe passages to cross roads. We analyzed the spatial relationship | 127 | safe passages to cross roads. We analyzed the spatial relationship | ||
| 128 | between road drainage elements (N\u202f=\u202f253; mostly culverts) as | 128 | between road drainage elements (N\u202f=\u202f253; mostly culverts) as | ||
| 129 | potential faunal\u00a0underpasses, and mortality due to vehicle | 129 | potential faunal\u00a0underpasses, and mortality due to vehicle | ||
| 130 | collisions in two\u00a0seasons\u00a0and on four relatively low-traffic | 130 | collisions in two\u00a0seasons\u00a0and on four relatively low-traffic | ||
| 131 | roads (<5000 cars/day) traversing oak\u00a0rangelands\u00a0of western | 131 | roads (<5000 cars/day) traversing oak\u00a0rangelands\u00a0of western | ||
| 132 | Andalusia (S Spain). Focusing on amphibians, reptiles and mammals, we | 132 | Andalusia (S Spain). Focusing on amphibians, reptiles and mammals, we | ||
| 133 | recorded and located casualties (N\u202f=\u202f238 individuals, 35 | 133 | recorded and located casualties (N\u202f=\u202f238 individuals, 35 | ||
| 134 | species) along these roads, identifying and characterizing all | 134 | species) along these roads, identifying and characterizing all | ||
| 135 | potential\u00a0underpasses. Overall frequencies of casualties and | 135 | potential\u00a0underpasses. Overall frequencies of casualties and | ||
| 136 | spatial distribution were highly variable both within and among these | 136 | spatial distribution were highly variable both within and among these | ||
| 137 | roads. We obtained an estimation of potential permeability for the | 137 | roads. We obtained an estimation of potential permeability for the | ||
| 138 | different roads. We detected, located and described a wide supply and | 138 | different roads. We detected, located and described a wide supply and | ||
| 139 | a very variable pattern of drainage culverts and other underpasses, | 139 | a very variable pattern of drainage culverts and other underpasses, | ||
| 140 | with differences among roads in passage attributes potentially | 140 | with differences among roads in passage attributes potentially | ||
| 141 | affecting permeability for wildlife, such as spatial arrangement, | 141 | affecting permeability for wildlife, such as spatial arrangement, | ||
| 142 | number, density (frequency or concentration of passages) and | 142 | number, density (frequency or concentration of passages) and | ||
| 143 | dimensions. We used Mantel tests to assess | 143 | dimensions. We used Mantel tests to assess | ||
| 144 | spatial\u00a0congruence\u00a0of passages and road-killed animals. We | 144 | spatial\u00a0congruence\u00a0of passages and road-killed animals. We | ||
| 145 | applied generalized linear mixed models fitted by maximum likelihood | 145 | applied generalized linear mixed models fitted by maximum likelihood | ||
| 146 | through\u00a0Akaike Information Criterion\u00a0to explain the | 146 | through\u00a0Akaike Information Criterion\u00a0to explain the | ||
| 147 | variation in the distance of the 238 casualties to the nearest | 147 | variation in the distance of the 238 casualties to the nearest | ||
| 148 | underpasses, with road transect and season as random factors, and | 148 | underpasses, with road transect and season as random factors, and | ||
| 149 | traffic intensity, speed and vertebrate class as\u00a0fixed effects. | 149 | traffic intensity, speed and vertebrate class as\u00a0fixed effects. | ||
| 150 | Both road-killed animals and underpass distribution followed | 150 | Both road-killed animals and underpass distribution followed | ||
| 151 | aggregated patterns, and casualties were not significantly related to | 151 | aggregated patterns, and casualties were not significantly related to | ||
| 152 | underpasses along any of the 4 roads. There were no differences in | 152 | underpasses along any of the 4 roads. There were no differences in | ||
| 153 | distance of casualties to the nearest underpass for the three | 153 | distance of casualties to the nearest underpass for the three | ||
| 154 | vertebrate classes. Although existing underpasses were abundant, we | 154 | vertebrate classes. Although existing underpasses were abundant, we | ||
| 155 | could not correlate potential permeability with reduced mortality | 155 | could not correlate potential permeability with reduced mortality | ||
| 156 | along these roads, and other factors potentially | 156 | along these roads, and other factors potentially | ||
| 157 | affecting\u00a0roadkill\u00a0aggregations should be evaluated along | 157 | affecting\u00a0roadkill\u00a0aggregations should be evaluated along | ||
| 158 | with permeability assessment. Mitigation of road-caused mortality can | 158 | with permeability assessment. Mitigation of road-caused mortality can | ||
| 159 | still be greatly improved for these roads, through measures of | 159 | still be greatly improved for these roads, through measures of | ||
| 160 | reconditioning and proper management of existing underpasses, aiming | 160 | reconditioning and proper management of existing underpasses, aiming | ||
| 161 | to maximize road permeability and reducing major impacts upon animal | 161 | to maximize road permeability and reducing major impacts upon animal | ||
| 162 | populations of Andalusian\u00a0rangelands.", | 162 | populations of Andalusian\u00a0rangelands.", | ||
| 163 | "es": "Road permeability to animal movements depends among several | 163 | "es": "Road permeability to animal movements depends among several | ||
| 164 | factors on structures which, integrated in the road design, operate as | 164 | factors on structures which, integrated in the road design, operate as | ||
| 165 | safe conducts to mitigate vehicle collision and barrier effects. There | 165 | safe conducts to mitigate vehicle collision and barrier effects. There | ||
| 166 | is abundant evidence that wildlife makes use of such structures as | 166 | is abundant evidence that wildlife makes use of such structures as | ||
| 167 | safe passages to cross roads. We analyzed the spatial relationship | 167 | safe passages to cross roads. We analyzed the spatial relationship | ||
| 168 | between road drainage elements (N = 253; mostly culverts) as potential | 168 | between road drainage elements (N = 253; mostly culverts) as potential | ||
| 169 | faunal underpasses, and mortality due to vehicle collisions in two | 169 | faunal underpasses, and mortality due to vehicle collisions in two | ||
| 170 | seasons and on four relatively low-traffic roads (<5000 cars/day) | 170 | seasons and on four relatively low-traffic roads (<5000 cars/day) | ||
| 171 | traversing oak rangelands of western Andalusia (S Spain). Focusing on | 171 | traversing oak rangelands of western Andalusia (S Spain). Focusing on | ||
| 172 | amphibians, reptiles and mammals, we recorded and located casualties | 172 | amphibians, reptiles and mammals, we recorded and located casualties | ||
| 173 | (N = 238 individuals, 35 species) along these roads, identifying and | 173 | (N = 238 individuals, 35 species) along these roads, identifying and | ||
| 174 | characterizing all potential underpasses. Overall frequencies of | 174 | characterizing all potential underpasses. Overall frequencies of | ||
| 175 | casualties and spatial distribution were highly variable both within | 175 | casualties and spatial distribution were highly variable both within | ||
| 176 | and among these roads. We obtained an estimation of potential | 176 | and among these roads. We obtained an estimation of potential | ||
| 177 | permeability for the different roads. We detected, located and | 177 | permeability for the different roads. We detected, located and | ||
| 178 | described a wide supply and a very variable pattern of drainage | 178 | described a wide supply and a very variable pattern of drainage | ||
| 179 | culverts and other underpasses, with differences among roads in | 179 | culverts and other underpasses, with differences among roads in | ||
| 180 | passage attributes potentially affecting permeability for wildlife, | 180 | passage attributes potentially affecting permeability for wildlife, | ||
| 181 | such as spatial arrangement, number, density (frequency or | 181 | such as spatial arrangement, number, density (frequency or | ||
| 182 | concentration of passages) and dimensions. We used Mantel tests to | 182 | concentration of passages) and dimensions. We used Mantel tests to | ||
| 183 | assess spatial congruence of passages and road-killed animals. We | 183 | assess spatial congruence of passages and road-killed animals. We | ||
| 184 | applied generalized linear mixed models fitted by maximum likelihood | 184 | applied generalized linear mixed models fitted by maximum likelihood | ||
| 185 | through Akaike Information Criterion to explain the variation in the | 185 | through Akaike Information Criterion to explain the variation in the | ||
| 186 | distance of the 238 casualties to the nearest underpasses, with road | 186 | distance of the 238 casualties to the nearest underpasses, with road | ||
| 187 | transect and season as random factors, and traffic intensity, speed | 187 | transect and season as random factors, and traffic intensity, speed | ||
| 188 | and vertebrate class as fixed effects. Both road-killed animals and | 188 | and vertebrate class as fixed effects. Both road-killed animals and | ||
| 189 | underpass distribution followed aggregated patterns, and casualties | 189 | underpass distribution followed aggregated patterns, and casualties | ||
| 190 | were not significantly related to underpasses along any of the 4 | 190 | were not significantly related to underpasses along any of the 4 | ||
| 191 | roads. There were no differences in distance of casualties to the | 191 | roads. There were no differences in distance of casualties to the | ||
| 192 | nearest underpass for the three vertebrate classes. Although existing | 192 | nearest underpass for the three vertebrate classes. Although existing | ||
| 193 | underpasses were abundant, we could not correlate potential | 193 | underpasses were abundant, we could not correlate potential | ||
| 194 | permeability with reduced mortality along these roads, and other | 194 | permeability with reduced mortality along these roads, and other | ||
| 195 | factors potentially affecting roadkill aggregations should be | 195 | factors potentially affecting roadkill aggregations should be | ||
| 196 | evaluated along with permeability assessment. Mitigation of | 196 | evaluated along with permeability assessment. Mitigation of | ||
| 197 | road-caused mortality can still be greatly improved for these roads, | 197 | road-caused mortality can still be greatly improved for these roads, | ||
| 198 | through measures of reconditioning and proper management of existing | 198 | through measures of reconditioning and proper management of existing | ||
| 199 | underpasses, aiming to maximize road permeability and reducing major | 199 | underpasses, aiming to maximize road permeability and reducing major | ||
| 200 | impacts upon animal populations of Andalusian rangelands." | 200 | impacts upon animal populations of Andalusian rangelands." | ||
| 201 | }, | 201 | }, | ||
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| 224 | "email": "buzon-bdatos@miteco.es", | 224 | "email": "buzon-bdatos@miteco.es", | ||
| 225 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 225 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 226 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 226 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
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