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En el instante 23 de junio de 2026, 15:46:07 UTC,
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Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Implications for conservation and game management of the roadkill levels of the endemic Iberian hare (Lepus granatensis).
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| 79 | "notes": "The Iberian hare (Lepus granatensis) is an important small | 79 | "notes": "The Iberian hare (Lepus granatensis) is an important small | ||
| 80 | game species endemic to the Iberian Peninsula for which the incidence | 80 | game species endemic to the Iberian Peninsula for which the incidence | ||
| 81 | of roadkill is unknown. We surveyed Iberian hare\u2013vehicle | 81 | of roadkill is unknown. We surveyed Iberian hare\u2013vehicle | ||
| 82 | accidents on road networks in southern Spain, focusing on roads that | 82 | accidents on road networks in southern Spain, focusing on roads that | ||
| 83 | mainly run through favorable habitats for this species: Mediterranean | 83 | mainly run through favorable habitats for this species: Mediterranean | ||
| 84 | landscapes with plots of arable crops, olive groves, and vineyards. We | 84 | landscapes with plots of arable crops, olive groves, and vineyards. We | ||
| 85 | recorded roadkills over a 5-month period, estimated hare accident | 85 | recorded roadkills over a 5-month period, estimated hare accident | ||
| 86 | densities on roads, and compared these numbers to hare hunting yields | 86 | densities on roads, and compared these numbers to hare hunting yields | ||
| 87 | in adjoining hunting estates. We also analyzed the spatial patterns of | 87 | in adjoining hunting estates. We also analyzed the spatial patterns of | ||
| 88 | and potential factors influencing hare roadkills. We detected the | 88 | and potential factors influencing hare roadkills. We detected the | ||
| 89 | existence of black spots for hare roadkills in areas with high | 89 | existence of black spots for hare roadkills in areas with high | ||
| 90 | landscape heterogeneity that also included embankments and nearby | 90 | landscape heterogeneity that also included embankments and nearby | ||
| 91 | crossroads and had high traffic intensity. Hare roadkill levels ranged | 91 | crossroads and had high traffic intensity. Hare roadkill levels ranged | ||
| 92 | from 5 to 25% of the annual harvest of hares killed on neighboring | 92 | from 5 to 25% of the annual harvest of hares killed on neighboring | ||
| 93 | hunting estates. We suggest that road collisions should be considered | 93 | hunting estates. We suggest that road collisions should be considered | ||
| 94 | in Iberian hare conservation in addition to hunting, since they may | 94 | in Iberian hare conservation in addition to hunting, since they may | ||
| 95 | represent an additive source of mortality. Game managers should | 95 | represent an additive source of mortality. Game managers should | ||
| 96 | address the issue of hare roadkill in harvest planning to compensate | 96 | address the issue of hare roadkill in harvest planning to compensate | ||
| 97 | for hare accidents, adjusting hunting quotas to account for this | 97 | for hare accidents, adjusting hunting quotas to account for this | ||
| 98 | unnatural source of mortality. Our results suggest future directions | 98 | unnatural source of mortality. Our results suggest future directions | ||
| 99 | for applied research in road ecology, including further work on | 99 | for applied research in road ecology, including further work on | ||
| 100 | demographic compensation and roadkill mitigation.", | 100 | demographic compensation and roadkill mitigation.", | ||
| 101 | "notes_translated": { | 101 | "notes_translated": { | ||
| 102 | "en": "The Iberian hare (Lepus granatensis) is an important small | 102 | "en": "The Iberian hare (Lepus granatensis) is an important small | ||
| 103 | game species endemic to the Iberian Peninsula for which the incidence | 103 | game species endemic to the Iberian Peninsula for which the incidence | ||
| 104 | of roadkill is unknown. We surveyed Iberian hare\u2013vehicle | 104 | of roadkill is unknown. We surveyed Iberian hare\u2013vehicle | ||
| 105 | accidents on road networks in southern Spain, focusing on roads that | 105 | accidents on road networks in southern Spain, focusing on roads that | ||
| 106 | mainly run through favorable habitats for this species: Mediterranean | 106 | mainly run through favorable habitats for this species: Mediterranean | ||
| 107 | landscapes with plots of arable crops, olive groves, and vineyards. We | 107 | landscapes with plots of arable crops, olive groves, and vineyards. We | ||
| 108 | recorded roadkills over a 5-month period, estimated hare accident | 108 | recorded roadkills over a 5-month period, estimated hare accident | ||
| 109 | densities on roads, and compared these numbers to hare hunting yields | 109 | densities on roads, and compared these numbers to hare hunting yields | ||
| 110 | in adjoining hunting estates. We also analyzed the spatial patterns of | 110 | in adjoining hunting estates. We also analyzed the spatial patterns of | ||
| 111 | and potential factors influencing hare roadkills. We detected the | 111 | and potential factors influencing hare roadkills. We detected the | ||
| 112 | existence of black spots for hare roadkills in areas with high | 112 | existence of black spots for hare roadkills in areas with high | ||
| 113 | landscape heterogeneity that also included embankments and nearby | 113 | landscape heterogeneity that also included embankments and nearby | ||
| 114 | crossroads and had high traffic intensity. Hare roadkill levels ranged | 114 | crossroads and had high traffic intensity. Hare roadkill levels ranged | ||
| 115 | from 5 to 25% of the annual harvest of hares killed on neighboring | 115 | from 5 to 25% of the annual harvest of hares killed on neighboring | ||
| 116 | hunting estates. We suggest that road collisions should be considered | 116 | hunting estates. We suggest that road collisions should be considered | ||
| 117 | in Iberian hare conservation in addition to hunting, since they may | 117 | in Iberian hare conservation in addition to hunting, since they may | ||
| 118 | represent an additive source of mortality. Game managers should | 118 | represent an additive source of mortality. Game managers should | ||
| 119 | address the issue of hare roadkill in harvest planning to compensate | 119 | address the issue of hare roadkill in harvest planning to compensate | ||
| 120 | for hare accidents, adjusting hunting quotas to account for this | 120 | for hare accidents, adjusting hunting quotas to account for this | ||
| 121 | unnatural source of mortality. Our results suggest future directions | 121 | unnatural source of mortality. Our results suggest future directions | ||
| 122 | for applied research in road ecology, including further work on | 122 | for applied research in road ecology, including further work on | ||
| 123 | demographic compensation and roadkill mitigation.", | 123 | demographic compensation and roadkill mitigation.", | ||
| 124 | "es": "The Iberian hare (Lepus granatensis) is an important small | 124 | "es": "The Iberian hare (Lepus granatensis) is an important small | ||
| 125 | game species endemic to the Iberian Peninsula for which the incidence | 125 | game species endemic to the Iberian Peninsula for which the incidence | ||
| 126 | of roadkill is unknown. We surveyed Iberian hare\u2013vehicle | 126 | of roadkill is unknown. We surveyed Iberian hare\u2013vehicle | ||
| 127 | accidents on road networks in southern Spain, focusing on roads that | 127 | accidents on road networks in southern Spain, focusing on roads that | ||
| 128 | mainly run through favorable habitats for this species: Mediterranean | 128 | mainly run through favorable habitats for this species: Mediterranean | ||
| 129 | landscapes with plots of arable crops, olive groves, and vineyards. We | 129 | landscapes with plots of arable crops, olive groves, and vineyards. We | ||
| 130 | recorded roadkills over a 5-month period, estimated hare accident | 130 | recorded roadkills over a 5-month period, estimated hare accident | ||
| 131 | densities on roads, and compared these numbers to hare hunting yields | 131 | densities on roads, and compared these numbers to hare hunting yields | ||
| 132 | in adjoining hunting estates. We also analyzed the spatial patterns of | 132 | in adjoining hunting estates. We also analyzed the spatial patterns of | ||
| 133 | and potential factors influencing hare roadkills. We detected the | 133 | and potential factors influencing hare roadkills. We detected the | ||
| 134 | existence of black spots for hare roadkills in areas with high | 134 | existence of black spots for hare roadkills in areas with high | ||
| 135 | landscape heterogeneity that also included embankments and nearby | 135 | landscape heterogeneity that also included embankments and nearby | ||
| 136 | crossroads and had high traffic intensity. Hare roadkill levels ranged | 136 | crossroads and had high traffic intensity. Hare roadkill levels ranged | ||
| 137 | from 5 to 25% of the annual harvest of hares killed on neighboring | 137 | from 5 to 25% of the annual harvest of hares killed on neighboring | ||
| 138 | hunting estates. We suggest that road collisions should be considered | 138 | hunting estates. We suggest that road collisions should be considered | ||
| 139 | in Iberian hare conservation in addition to hunting, since they may | 139 | in Iberian hare conservation in addition to hunting, since they may | ||
| 140 | represent an additive source of mortality. Game managers should | 140 | represent an additive source of mortality. Game managers should | ||
| 141 | address the issue of hare roadkill in harvest planning to compensate | 141 | address the issue of hare roadkill in harvest planning to compensate | ||
| 142 | for hare accidents, adjusting hunting quotas to account for this | 142 | for hare accidents, adjusting hunting quotas to account for this | ||
| 143 | unnatural source of mortality. Our results suggest future directions | 143 | unnatural source of mortality. Our results suggest future directions | ||
| 144 | for applied research in road ecology, including further work on | 144 | for applied research in road ecology, including further work on | ||
| 145 | demographic compensation and roadkill mitigation." | 145 | demographic compensation and roadkill mitigation." | ||
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