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spatial_coverage
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en General versus specific surveys: estimating the suitability of different road-crossing structures for small mammals.
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| 5 | "author": "D'Amico, M., Clevenger, A.P., Rom\u00e1n, J. y Revilla, | 5 | "author": "D'Amico, M., Clevenger, A.P., Rom\u00e1n, J. y Revilla, | ||
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| 60 | "The Journal of Wildlife Management. Vol. 79", | 60 | "The Journal of Wildlife Management. Vol. 79", | ||
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| 82 | "notes": "The use of wildlife road\u2010crossing structures (WCS | 82 | "notes": "The use of wildlife road\u2010crossing structures (WCS | ||
| 83 | hereafter) is less monitored for small mammals than for more | 83 | hereafter) is less monitored for small mammals than for more | ||
| 84 | emblematic species. Furthermore, because of the undeniable difficulty | 84 | emblematic species. Furthermore, because of the undeniable difficulty | ||
| 85 | of small\u2010mammal track identification, most biologists usually | 85 | of small\u2010mammal track identification, most biologists usually | ||
| 86 | carry out general surveys without species recognition. We hypothesized | 86 | carry out general surveys without species recognition. We hypothesized | ||
| 87 | that general surveys traditionally used for monitoring WRC by small | 87 | that general surveys traditionally used for monitoring WRC by small | ||
| 88 | mammals may be biased because the degraded habitats along roads are | 88 | mammals may be biased because the degraded habitats along roads are | ||
| 89 | mainly used by generalist and not specialist species. For this reason, | 89 | mainly used by generalist and not specialist species. For this reason, | ||
| 90 | we compared the results of a general small\u2010mammal survey with | 90 | we compared the results of a general small\u2010mammal survey with | ||
| 91 | those from a species\u2010specific one, focusing on 3 study species: 1 | 91 | those from a species\u2010specific one, focusing on 3 study species: 1 | ||
| 92 | habitat generalist (North American deer mouse [Peromyscus | 92 | habitat generalist (North American deer mouse [Peromyscus | ||
| 93 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | 93 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | ||
| 94 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | 94 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | ||
| 95 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | 95 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | ||
| 96 | open\u2010span underpasses, and both elliptical and box culverts) in | 96 | open\u2010span underpasses, and both elliptical and box culverts) in | ||
| 97 | Banff National Park (Canada), by placing footprint track tubes along | 97 | Banff National Park (Canada), by placing footprint track tubes along | ||
| 98 | the WCS, and as a reference in front of their entrances (mainly | 98 | the WCS, and as a reference in front of their entrances (mainly | ||
| 99 | located in roadside grasslands) and in the surrounding woodlands. | 99 | located in roadside grasslands) and in the surrounding woodlands. | ||
| 100 | Using the traditional general survey, we did not detect significant | 100 | Using the traditional general survey, we did not detect significant | ||
| 101 | differences in small\u2010mammal presence among WCS and reference | 101 | differences in small\u2010mammal presence among WCS and reference | ||
| 102 | sites. In contrast, species\u2010specific surveys showed that only the | 102 | sites. In contrast, species\u2010specific surveys showed that only the | ||
| 103 | deer mouse (a generalist species) consistently used the WCS. The deer | 103 | deer mouse (a generalist species) consistently used the WCS. The deer | ||
| 104 | mice did not show preferences for any WCS type, whereas the specialist | 104 | mice did not show preferences for any WCS type, whereas the specialist | ||
| 105 | species (voles) used only overpasses. Therefore, general surveys used | 105 | species (voles) used only overpasses. Therefore, general surveys used | ||
| 106 | without species identification can underestimate the value of WCS for | 106 | without species identification can underestimate the value of WCS for | ||
| 107 | specialist small mammals, with relevant conservation implications. As | 107 | specialist small mammals, with relevant conservation implications. As | ||
| 108 | a consequence, we recommend species\u2010specific surveys of WCS | 108 | a consequence, we recommend species\u2010specific surveys of WCS | ||
| 109 | suitability for small mammals. We also suggest improving the habitat | 109 | suitability for small mammals. We also suggest improving the habitat | ||
| 110 | (or at least the cover availability) in the WCS and along the space | 110 | (or at least the cover availability) in the WCS and along the space | ||
| 111 | between them and the surrounding environments to increase WCS | 111 | between them and the surrounding environments to increase WCS | ||
| 112 | suitability for specialist species. \n Palabras clave: Mammal", | 112 | suitability for specialist species. \n Palabras clave: Mammal", | ||
| 113 | "notes_translated": { | 113 | "notes_translated": { | ||
| 114 | "en": "The use of wildlife road\u2010crossing structures (WCS | 114 | "en": "The use of wildlife road\u2010crossing structures (WCS | ||
| 115 | hereafter) is less monitored for small mammals than for more | 115 | hereafter) is less monitored for small mammals than for more | ||
| 116 | emblematic species. Furthermore, because of the undeniable difficulty | 116 | emblematic species. Furthermore, because of the undeniable difficulty | ||
| 117 | of small\u2010mammal track identification, most biologists usually | 117 | of small\u2010mammal track identification, most biologists usually | ||
| 118 | carry out general surveys without species recognition. We hypothesized | 118 | carry out general surveys without species recognition. We hypothesized | ||
| 119 | that general surveys traditionally used for monitoring WRC by small | 119 | that general surveys traditionally used for monitoring WRC by small | ||
| 120 | mammals may be biased because the degraded habitats along roads are | 120 | mammals may be biased because the degraded habitats along roads are | ||
| 121 | mainly used by generalist and not specialist species. For this reason, | 121 | mainly used by generalist and not specialist species. For this reason, | ||
| 122 | we compared the results of a general small\u2010mammal survey with | 122 | we compared the results of a general small\u2010mammal survey with | ||
| 123 | those from a species\u2010specific one, focusing on 3 study species: 1 | 123 | those from a species\u2010specific one, focusing on 3 study species: 1 | ||
| 124 | habitat generalist (North American deer mouse [Peromyscus | 124 | habitat generalist (North American deer mouse [Peromyscus | ||
| 125 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | 125 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | ||
| 126 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | 126 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | ||
| 127 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | 127 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | ||
| 128 | open\u2010span underpasses, and both elliptical and box culverts) in | 128 | open\u2010span underpasses, and both elliptical and box culverts) in | ||
| 129 | Banff National Park (Canada), by placing footprint track tubes along | 129 | Banff National Park (Canada), by placing footprint track tubes along | ||
| 130 | the WCS, and as a reference in front of their entrances (mainly | 130 | the WCS, and as a reference in front of their entrances (mainly | ||
| 131 | located in roadside grasslands) and in the surrounding woodlands. | 131 | located in roadside grasslands) and in the surrounding woodlands. | ||
| 132 | Using the traditional general survey, we did not detect significant | 132 | Using the traditional general survey, we did not detect significant | ||
| 133 | differences in small\u2010mammal presence among WCS and reference | 133 | differences in small\u2010mammal presence among WCS and reference | ||
| 134 | sites. In contrast, species\u2010specific surveys showed that only the | 134 | sites. In contrast, species\u2010specific surveys showed that only the | ||
| 135 | deer mouse (a generalist species) consistently used the WCS. The deer | 135 | deer mouse (a generalist species) consistently used the WCS. The deer | ||
| 136 | mice did not show preferences for any WCS type, whereas the specialist | 136 | mice did not show preferences for any WCS type, whereas the specialist | ||
| 137 | species (voles) used only overpasses. Therefore, general surveys used | 137 | species (voles) used only overpasses. Therefore, general surveys used | ||
| 138 | without species identification can underestimate the value of WCS for | 138 | without species identification can underestimate the value of WCS for | ||
| 139 | specialist small mammals, with relevant conservation implications. As | 139 | specialist small mammals, with relevant conservation implications. As | ||
| 140 | a consequence, we recommend species\u2010specific surveys of WCS | 140 | a consequence, we recommend species\u2010specific surveys of WCS | ||
| 141 | suitability for small mammals. We also suggest improving the habitat | 141 | suitability for small mammals. We also suggest improving the habitat | ||
| 142 | (or at least the cover availability) in the WCS and along the space | 142 | (or at least the cover availability) in the WCS and along the space | ||
| 143 | between them and the surrounding environments to increase WCS | 143 | between them and the surrounding environments to increase WCS | ||
| 144 | suitability for specialist species. \u00a9 2015 The Wildlife | 144 | suitability for specialist species. \u00a9 2015 The Wildlife | ||
| 145 | Society.", | 145 | Society.", | ||
| 146 | "es": "The use of wildlife road\u2010crossing structures (WCS | 146 | "es": "The use of wildlife road\u2010crossing structures (WCS | ||
| 147 | hereafter) is less monitored for small mammals than for more | 147 | hereafter) is less monitored for small mammals than for more | ||
| 148 | emblematic species. Furthermore, because of the undeniable difficulty | 148 | emblematic species. Furthermore, because of the undeniable difficulty | ||
| 149 | of small\u2010mammal track identification, most biologists usually | 149 | of small\u2010mammal track identification, most biologists usually | ||
| 150 | carry out general surveys without species recognition. We hypothesized | 150 | carry out general surveys without species recognition. We hypothesized | ||
| 151 | that general surveys traditionally used for monitoring WRC by small | 151 | that general surveys traditionally used for monitoring WRC by small | ||
| 152 | mammals may be biased because the degraded habitats along roads are | 152 | mammals may be biased because the degraded habitats along roads are | ||
| 153 | mainly used by generalist and not specialist species. For this reason, | 153 | mainly used by generalist and not specialist species. For this reason, | ||
| 154 | we compared the results of a general small\u2010mammal survey with | 154 | we compared the results of a general small\u2010mammal survey with | ||
| 155 | those from a species\u2010specific one, focusing on 3 study species: 1 | 155 | those from a species\u2010specific one, focusing on 3 study species: 1 | ||
| 156 | habitat generalist (North American deer mouse [Peromyscus | 156 | habitat generalist (North American deer mouse [Peromyscus | ||
| 157 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | 157 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | ||
| 158 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | 158 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | ||
| 159 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | 159 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | ||
| 160 | open\u2010span underpasses, and both elliptical and box culverts) in | 160 | open\u2010span underpasses, and both elliptical and box culverts) in | ||
| 161 | Banff National Park (Canada), by placing footprint track tubes along | 161 | Banff National Park (Canada), by placing footprint track tubes along | ||
| 162 | the WCS, and as a reference in front of their entrances (mainly | 162 | the WCS, and as a reference in front of their entrances (mainly | ||
| 163 | located in roadside grasslands) and in the surrounding woodlands. | 163 | located in roadside grasslands) and in the surrounding woodlands. | ||
| 164 | Using the traditional general survey, we did not detect significant | 164 | Using the traditional general survey, we did not detect significant | ||
| 165 | differences in small\u2010mammal presence among WCS and reference | 165 | differences in small\u2010mammal presence among WCS and reference | ||
| 166 | sites. In contrast, species\u2010specific surveys showed that only the | 166 | sites. In contrast, species\u2010specific surveys showed that only the | ||
| 167 | deer mouse (a generalist species) consistently used the WCS. The deer | 167 | deer mouse (a generalist species) consistently used the WCS. The deer | ||
| 168 | mice did not show preferences for any WCS type, whereas the specialist | 168 | mice did not show preferences for any WCS type, whereas the specialist | ||
| 169 | species (voles) used only overpasses. Therefore, general surveys used | 169 | species (voles) used only overpasses. Therefore, general surveys used | ||
| 170 | without species identification can underestimate the value of WCS for | 170 | without species identification can underestimate the value of WCS for | ||
| 171 | specialist small mammals, with relevant conservation implications. As | 171 | specialist small mammals, with relevant conservation implications. As | ||
| 172 | a consequence, we recommend species\u2010specific surveys of WCS | 172 | a consequence, we recommend species\u2010specific surveys of WCS | ||
| 173 | suitability for small mammals. We also suggest improving the habitat | 173 | suitability for small mammals. We also suggest improving the habitat | ||
| 174 | (or at least the cover availability) in the WCS and along the space | 174 | (or at least the cover availability) in the WCS and along the space | ||
| 175 | between them and the surrounding environments to increase WCS | 175 | between them and the surrounding environments to increase WCS | ||
| 176 | suitability for specialist species. \n Palabras clave: Mammal" | 176 | suitability for specialist species. \n Palabras clave: Mammal" | ||
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