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En el instante 25 de junio de 2026, 12:36:16 UTC,
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Modificado el valor del campo
modified
a2026-06-25
en Use of road verges by butterfly and burnet populations, and the effect of roads on adult dispersal and mortality. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Use of road verges by butterfly and burnet populations, and the effect of roads on adult dispersal and mortality.
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| 79 | "notes": "Transects made beside 12 main roads in Dorset and | 93 | "notes": "Transects made beside 12 main roads in Dorset and | ||
| 80 | Hampshire (UK) showed that verges and central reservations supported a | 94 | Hampshire (UK) showed that verges and central reservations supported a | ||
| 81 | wide variety of butterflies and burnets (Zygaenidae). One site had 23 | 95 | wide variety of butterflies and burnets (Zygaenidae). One site had 23 | ||
| 82 | species of butterfly (=40% of British species), while the average was | 96 | species of butterfly (=40% of British species), while the average was | ||
| 83 | nine (16%) species per 100-m transect. Most were common species, but | 97 | nine (16%) species per 100-m transect. Most were common species, but | ||
| 84 | some rarities were present. Mark-recapture estimates of adult | 98 | some rarities were present. Mark-recapture estimates of adult | ||
| 85 | densities on verges were up to 2774 adults ha-1 for Maniola jurtina. | 99 | densities on verges were up to 2774 adults ha-1 for Maniola jurtina. | ||
| 86 | Populations of Melanargia galathea, Pieris rapae and Polyommatus | 100 | Populations of Melanargia galathea, Pieris rapae and Polyommatus | ||
| 87 | icarus were large or medium-sized for these species. Variation in the | 101 | icarus were large or medium-sized for these species. Variation in the | ||
| 88 | number of species, density and diversity of butterflies and burnets | 102 | number of species, density and diversity of butterflies and burnets | ||
| 89 | depended on the range of breeding habitats on verges. The density of | 103 | depended on the range of breeding habitats on verges. The density of | ||
| 90 | adults and number of species were correlated with verge width, while | 104 | adults and number of species were correlated with verge width, while | ||
| 91 | diversity was correlated with the abundance of nectar. The amount of | 105 | diversity was correlated with the abundance of nectar. The amount of | ||
| 92 | traffic had no apparent effect on populations on verges. Road verges | 106 | traffic had no apparent effect on populations on verges. Road verges | ||
| 93 | could be substantially improved for butterflies and burnets by | 107 | could be substantially improved for butterflies and burnets by | ||
| 94 | reducing the depth of top soil and amount of fertilizer applied, by | 108 | reducing the depth of top soil and amount of fertilizer applied, by | ||
| 95 | planting with native seed mixes and shrubs, by creating an irregular | 109 | planting with native seed mixes and shrubs, by creating an irregular | ||
| 96 | topography and surrounding them with hedges, and by making verges and | 110 | topography and surrounding them with hedges, and by making verges and | ||
| 97 | central reservations as wide as possible. Wide busy roads were no | 111 | central reservations as wide as possible. Wide busy roads were no | ||
| 98 | barrier to the movements of species living in open populations, but | 112 | barrier to the movements of species living in open populations, but | ||
| 99 | slightly impeded those with closed populations. Mark-recapture showed | 113 | slightly impeded those with closed populations. Mark-recapture showed | ||
| 100 | that 10-30% of adults of three species with closed populations crossed | 114 | that 10-30% of adults of three species with closed populations crossed | ||
| 101 | the road. Roads cannot be considered as a barrier to gene flow in any | 115 | the road. Roads cannot be considered as a barrier to gene flow in any | ||
| 102 | species in this study. Vehicles killed 0\u00b76-1\u00b79% of adults of | 116 | species in this study. Vehicles killed 0\u00b76-1\u00b79% of adults of | ||
| 103 | species from closed populations, and about 7% of those from open | 117 | species from closed populations, and about 7% of those from open | ||
| 104 | populations. These mortalities were insignificant compared to those | 118 | populations. These mortalities were insignificant compared to those | ||
| 105 | caused by natural factors.\n Palabras clave: Butterfly, Dispersal, | 119 | caused by natural factors.\n Palabras clave: Butterfly, Dispersal, | ||
| 106 | Monitoring, Mortality, Population, Verge", | 120 | Monitoring, Mortality, Population, Verge", | ||
| 107 | "notes_translated": { | 121 | "notes_translated": { | ||
| 108 | "en": "1. Transects made beside 12 main roads in Dorset and | 122 | "en": "1. Transects made beside 12 main roads in Dorset and | ||
| 109 | Hampshire (UK) showed that verges and central reservations supported a | 123 | Hampshire (UK) showed that verges and central reservations supported a | ||
| 110 | wide variety of butterflies and burnets (Zygaenidae). One site had 23 | 124 | wide variety of butterflies and burnets (Zygaenidae). One site had 23 | ||
| 111 | species of butterfly (=40% of British species), while the average was | 125 | species of butterfly (=40% of British species), while the average was | ||
| 112 | nine (16%) species per 100-m transect. Most were common species, but | 126 | nine (16%) species per 100-m transect. Most were common species, but | ||
| 113 | some rarities were present. 2. Mark-recapture estimates of adult | 127 | some rarities were present. 2. Mark-recapture estimates of adult | ||
| 114 | densities on verges were up to 2774 adults ha-1 for Maniola jurtina. | 128 | densities on verges were up to 2774 adults ha-1 for Maniola jurtina. | ||
| 115 | Populations of Melanargia galathea, Pieris rapae and Polyommatus | 129 | Populations of Melanargia galathea, Pieris rapae and Polyommatus | ||
| 116 | icarus were large or medium-sized for these species. 3. Variation in | 130 | icarus were large or medium-sized for these species. 3. Variation in | ||
| 117 | the number of species, density and diversity of butterflies and | 131 | the number of species, density and diversity of butterflies and | ||
| 118 | burnets depended on the range of breeding habitats on verges. The | 132 | burnets depended on the range of breeding habitats on verges. The | ||
| 119 | density of adults and number of species were correlated with verge | 133 | density of adults and number of species were correlated with verge | ||
| 120 | width, while diversity was correlated with the abundance of nectar. | 134 | width, while diversity was correlated with the abundance of nectar. | ||
| 121 | The amount of traffic had no apparent effect on \u2026", | 135 | The amount of traffic had no apparent effect on \u2026", | ||
| 122 | "es": "Transects made beside 12 main roads in Dorset and Hampshire | 136 | "es": "Transects made beside 12 main roads in Dorset and Hampshire | ||
| 123 | (UK) showed that verges and central reservations supported a wide | 137 | (UK) showed that verges and central reservations supported a wide | ||
| 124 | variety of butterflies and burnets (Zygaenidae). One site had 23 | 138 | variety of butterflies and burnets (Zygaenidae). One site had 23 | ||
| 125 | species of butterfly (=40% of British species), while the average was | 139 | species of butterfly (=40% of British species), while the average was | ||
| 126 | nine (16%) species per 100-m transect. Most were common species, but | 140 | nine (16%) species per 100-m transect. Most were common species, but | ||
| 127 | some rarities were present. Mark-recapture estimates of adult | 141 | some rarities were present. Mark-recapture estimates of adult | ||
| 128 | densities on verges were up to 2774 adults ha-1 for Maniola jurtina. | 142 | densities on verges were up to 2774 adults ha-1 for Maniola jurtina. | ||
| 129 | Populations of Melanargia galathea, Pieris rapae and Polyommatus | 143 | Populations of Melanargia galathea, Pieris rapae and Polyommatus | ||
| 130 | icarus were large or medium-sized for these species. Variation in the | 144 | icarus were large or medium-sized for these species. Variation in the | ||
| 131 | number of species, density and diversity of butterflies and burnets | 145 | number of species, density and diversity of butterflies and burnets | ||
| 132 | depended on the range of breeding habitats on verges. The density of | 146 | depended on the range of breeding habitats on verges. The density of | ||
| 133 | adults and number of species were correlated with verge width, while | 147 | adults and number of species were correlated with verge width, while | ||
| 134 | diversity was correlated with the abundance of nectar. The amount of | 148 | diversity was correlated with the abundance of nectar. The amount of | ||
| 135 | traffic had no apparent effect on populations on verges. Road verges | 149 | traffic had no apparent effect on populations on verges. Road verges | ||
| 136 | could be substantially improved for butterflies and burnets by | 150 | could be substantially improved for butterflies and burnets by | ||
| 137 | reducing the depth of top soil and amount of fertilizer applied, by | 151 | reducing the depth of top soil and amount of fertilizer applied, by | ||
| 138 | planting with native seed mixes and shrubs, by creating an irregular | 152 | planting with native seed mixes and shrubs, by creating an irregular | ||
| 139 | topography and surrounding them with hedges, and by making verges and | 153 | topography and surrounding them with hedges, and by making verges and | ||
| 140 | central reservations as wide as possible. Wide busy roads were no | 154 | central reservations as wide as possible. Wide busy roads were no | ||
| 141 | barrier to the movements of species living in open populations, but | 155 | barrier to the movements of species living in open populations, but | ||
| 142 | slightly impeded those with closed populations. Mark-recapture showed | 156 | slightly impeded those with closed populations. Mark-recapture showed | ||
| 143 | that 10-30% of adults of three species with closed populations crossed | 157 | that 10-30% of adults of three species with closed populations crossed | ||
| 144 | the road. Roads cannot be considered as a barrier to gene flow in any | 158 | the road. Roads cannot be considered as a barrier to gene flow in any | ||
| 145 | species in this study. Vehicles killed 0\u00b76-1\u00b79% of adults of | 159 | species in this study. Vehicles killed 0\u00b76-1\u00b79% of adults of | ||
| 146 | species from closed populations, and about 7% of those from open | 160 | species from closed populations, and about 7% of those from open | ||
| 147 | populations. These mortalities were insignificant compared to those | 161 | populations. These mortalities were insignificant compared to those | ||
| 148 | caused by natural factors.\n Palabras clave: Butterfly, Dispersal, | 162 | caused by natural factors.\n Palabras clave: Butterfly, Dispersal, | ||
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| 281 | "name": "dispersion", | 295 | "name": "dispersion", | ||
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| 319 | }, | 333 | }, | ||
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| 333 | ], | 347 | ], | ||
| 334 | "title": "Use of road verges by butterfly and burnet populations, | 348 | "title": "Use of road verges by butterfly and burnet populations, | ||
| 335 | and the effect of roads on adult dispersal and mortality.", | 349 | and the effect of roads on adult dispersal and mortality.", | ||
| 336 | "title_translated": { | 350 | "title_translated": { | ||
| 337 | "en": "", | 351 | "en": "", | ||
| 338 | "es": "Use of road verges by butterfly and burnet populations, and | 352 | "es": "Use of road verges by butterfly and burnet populations, and | ||
| 339 | the effect of roads on adult dispersal and mortality." | 353 | the effect of roads on adult dispersal and mortality." | ||
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| 343 | "type": "dataset", | 357 | "type": "dataset", | ||
| 344 | "url": | 358 | "url": | ||
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