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) en General versus specific surveys: estimating the suitability of different road-crossing structures for small mammals.
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| 81 | "name": "b683b75f-949f-5d85-adf6-328c403a8a83", | 95 | "name": "b683b75f-949f-5d85-adf6-328c403a8a83", | ||
| 82 | "notes": "The use of wildlife road\u2010crossing structures (WCS | 96 | "notes": "The use of wildlife road\u2010crossing structures (WCS | ||
| 83 | hereafter) is less monitored for small mammals than for more | 97 | hereafter) is less monitored for small mammals than for more | ||
| 84 | emblematic species. Furthermore, because of the undeniable difficulty | 98 | emblematic species. Furthermore, because of the undeniable difficulty | ||
| 85 | of small\u2010mammal track identification, most biologists usually | 99 | of small\u2010mammal track identification, most biologists usually | ||
| 86 | carry out general surveys without species recognition. We hypothesized | 100 | carry out general surveys without species recognition. We hypothesized | ||
| 87 | that general surveys traditionally used for monitoring WRC by small | 101 | that general surveys traditionally used for monitoring WRC by small | ||
| 88 | mammals may be biased because the degraded habitats along roads are | 102 | mammals may be biased because the degraded habitats along roads are | ||
| 89 | mainly used by generalist and not specialist species. For this reason, | 103 | mainly used by generalist and not specialist species. For this reason, | ||
| 90 | we compared the results of a general small\u2010mammal survey with | 104 | we compared the results of a general small\u2010mammal survey with | ||
| 91 | those from a species\u2010specific one, focusing on 3 study species: 1 | 105 | those from a species\u2010specific one, focusing on 3 study species: 1 | ||
| 92 | habitat generalist (North American deer mouse [Peromyscus | 106 | habitat generalist (North American deer mouse [Peromyscus | ||
| 93 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | 107 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | ||
| 94 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | 108 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | ||
| 95 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | 109 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | ||
| 96 | open\u2010span underpasses, and both elliptical and box culverts) in | 110 | open\u2010span underpasses, and both elliptical and box culverts) in | ||
| 97 | Banff National Park (Canada), by placing footprint track tubes along | 111 | Banff National Park (Canada), by placing footprint track tubes along | ||
| 98 | the WCS, and as a reference in front of their entrances (mainly | 112 | the WCS, and as a reference in front of their entrances (mainly | ||
| 99 | located in roadside grasslands) and in the surrounding woodlands. | 113 | located in roadside grasslands) and in the surrounding woodlands. | ||
| 100 | Using the traditional general survey, we did not detect significant | 114 | Using the traditional general survey, we did not detect significant | ||
| 101 | differences in small\u2010mammal presence among WCS and reference | 115 | differences in small\u2010mammal presence among WCS and reference | ||
| 102 | sites. In contrast, species\u2010specific surveys showed that only the | 116 | sites. In contrast, species\u2010specific surveys showed that only the | ||
| 103 | deer mouse (a generalist species) consistently used the WCS. The deer | 117 | deer mouse (a generalist species) consistently used the WCS. The deer | ||
| 104 | mice did not show preferences for any WCS type, whereas the specialist | 118 | mice did not show preferences for any WCS type, whereas the specialist | ||
| 105 | species (voles) used only overpasses. Therefore, general surveys used | 119 | species (voles) used only overpasses. Therefore, general surveys used | ||
| 106 | without species identification can underestimate the value of WCS for | 120 | without species identification can underestimate the value of WCS for | ||
| 107 | specialist small mammals, with relevant conservation implications. As | 121 | specialist small mammals, with relevant conservation implications. As | ||
| 108 | a consequence, we recommend species\u2010specific surveys of WCS | 122 | a consequence, we recommend species\u2010specific surveys of WCS | ||
| 109 | suitability for small mammals. We also suggest improving the habitat | 123 | suitability for small mammals. We also suggest improving the habitat | ||
| 110 | (or at least the cover availability) in the WCS and along the space | 124 | (or at least the cover availability) in the WCS and along the space | ||
| 111 | between them and the surrounding environments to increase WCS | 125 | between them and the surrounding environments to increase WCS | ||
| 112 | suitability for specialist species. \n Palabras clave: Mammal", | 126 | suitability for specialist species. \n Palabras clave: Mammal", | ||
| 113 | "notes_translated": { | 127 | "notes_translated": { | ||
| 114 | "en": "The use of wildlife road\u2010crossing structures (WCS | 128 | "en": "The use of wildlife road\u2010crossing structures (WCS | ||
| 115 | hereafter) is less monitored for small mammals than for more | 129 | hereafter) is less monitored for small mammals than for more | ||
| 116 | emblematic species. Furthermore, because of the undeniable difficulty | 130 | emblematic species. Furthermore, because of the undeniable difficulty | ||
| 117 | of small\u2010mammal track identification, most biologists usually | 131 | of small\u2010mammal track identification, most biologists usually | ||
| 118 | carry out general surveys without species recognition. We hypothesized | 132 | carry out general surveys without species recognition. We hypothesized | ||
| 119 | that general surveys traditionally used for monitoring WRC by small | 133 | that general surveys traditionally used for monitoring WRC by small | ||
| 120 | mammals may be biased because the degraded habitats along roads are | 134 | mammals may be biased because the degraded habitats along roads are | ||
| 121 | mainly used by generalist and not specialist species. For this reason, | 135 | mainly used by generalist and not specialist species. For this reason, | ||
| 122 | we compared the results of a general small\u2010mammal survey with | 136 | we compared the results of a general small\u2010mammal survey with | ||
| 123 | those from a species\u2010specific one, focusing on 3 study species: 1 | 137 | those from a species\u2010specific one, focusing on 3 study species: 1 | ||
| 124 | habitat generalist (North American deer mouse [Peromyscus | 138 | habitat generalist (North American deer mouse [Peromyscus | ||
| 125 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | 139 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | ||
| 126 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | 140 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | ||
| 127 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | 141 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | ||
| 128 | open\u2010span underpasses, and both elliptical and box culverts) in | 142 | open\u2010span underpasses, and both elliptical and box culverts) in | ||
| 129 | Banff National Park (Canada), by placing footprint track tubes along | 143 | Banff National Park (Canada), by placing footprint track tubes along | ||
| 130 | the WCS, and as a reference in front of their entrances (mainly | 144 | the WCS, and as a reference in front of their entrances (mainly | ||
| 131 | located in roadside grasslands) and in the surrounding woodlands. | 145 | located in roadside grasslands) and in the surrounding woodlands. | ||
| 132 | Using the traditional general survey, we did not detect significant | 146 | Using the traditional general survey, we did not detect significant | ||
| 133 | differences in small\u2010mammal presence among WCS and reference | 147 | differences in small\u2010mammal presence among WCS and reference | ||
| 134 | sites. In contrast, species\u2010specific surveys showed that only the | 148 | sites. In contrast, species\u2010specific surveys showed that only the | ||
| 135 | deer mouse (a generalist species) consistently used the WCS. The deer | 149 | deer mouse (a generalist species) consistently used the WCS. The deer | ||
| 136 | mice did not show preferences for any WCS type, whereas the specialist | 150 | mice did not show preferences for any WCS type, whereas the specialist | ||
| 137 | species (voles) used only overpasses. Therefore, general surveys used | 151 | species (voles) used only overpasses. Therefore, general surveys used | ||
| 138 | without species identification can underestimate the value of WCS for | 152 | without species identification can underestimate the value of WCS for | ||
| 139 | specialist small mammals, with relevant conservation implications. As | 153 | specialist small mammals, with relevant conservation implications. As | ||
| 140 | a consequence, we recommend species\u2010specific surveys of WCS | 154 | a consequence, we recommend species\u2010specific surveys of WCS | ||
| 141 | suitability for small mammals. We also suggest improving the habitat | 155 | suitability for small mammals. We also suggest improving the habitat | ||
| 142 | (or at least the cover availability) in the WCS and along the space | 156 | (or at least the cover availability) in the WCS and along the space | ||
| 143 | between them and the surrounding environments to increase WCS | 157 | between them and the surrounding environments to increase WCS | ||
| 144 | suitability for specialist species. \u00a9 2015 The Wildlife | 158 | suitability for specialist species. \u00a9 2015 The Wildlife | ||
| 145 | Society.", | 159 | Society.", | ||
| 146 | "es": "The use of wildlife road\u2010crossing structures (WCS | 160 | "es": "The use of wildlife road\u2010crossing structures (WCS | ||
| 147 | hereafter) is less monitored for small mammals than for more | 161 | hereafter) is less monitored for small mammals than for more | ||
| 148 | emblematic species. Furthermore, because of the undeniable difficulty | 162 | emblematic species. Furthermore, because of the undeniable difficulty | ||
| 149 | of small\u2010mammal track identification, most biologists usually | 163 | of small\u2010mammal track identification, most biologists usually | ||
| 150 | carry out general surveys without species recognition. We hypothesized | 164 | carry out general surveys without species recognition. We hypothesized | ||
| 151 | that general surveys traditionally used for monitoring WRC by small | 165 | that general surveys traditionally used for monitoring WRC by small | ||
| 152 | mammals may be biased because the degraded habitats along roads are | 166 | mammals may be biased because the degraded habitats along roads are | ||
| 153 | mainly used by generalist and not specialist species. For this reason, | 167 | mainly used by generalist and not specialist species. For this reason, | ||
| 154 | we compared the results of a general small\u2010mammal survey with | 168 | we compared the results of a general small\u2010mammal survey with | ||
| 155 | those from a species\u2010specific one, focusing on 3 study species: 1 | 169 | those from a species\u2010specific one, focusing on 3 study species: 1 | ||
| 156 | habitat generalist (North American deer mouse [Peromyscus | 170 | habitat generalist (North American deer mouse [Peromyscus | ||
| 157 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | 171 | maniculatus]), 1 forest specialist (southern red\u2010backed vole | ||
| 158 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | 172 | [Myodes gapperi]), and 1 prairie specialist (meadow vole [Microtus | ||
| 159 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | 173 | pennsylvanicus]). We sampled along 4 types of WCS (overpasses, | ||
| 160 | open\u2010span underpasses, and both elliptical and box culverts) in | 174 | open\u2010span underpasses, and both elliptical and box culverts) in | ||
| 161 | Banff National Park (Canada), by placing footprint track tubes along | 175 | Banff National Park (Canada), by placing footprint track tubes along | ||
| 162 | the WCS, and as a reference in front of their entrances (mainly | 176 | the WCS, and as a reference in front of their entrances (mainly | ||
| 163 | located in roadside grasslands) and in the surrounding woodlands. | 177 | located in roadside grasslands) and in the surrounding woodlands. | ||
| 164 | Using the traditional general survey, we did not detect significant | 178 | Using the traditional general survey, we did not detect significant | ||
| 165 | differences in small\u2010mammal presence among WCS and reference | 179 | differences in small\u2010mammal presence among WCS and reference | ||
| 166 | sites. In contrast, species\u2010specific surveys showed that only the | 180 | sites. In contrast, species\u2010specific surveys showed that only the | ||
| 167 | deer mouse (a generalist species) consistently used the WCS. The deer | 181 | deer mouse (a generalist species) consistently used the WCS. The deer | ||
| 168 | mice did not show preferences for any WCS type, whereas the specialist | 182 | mice did not show preferences for any WCS type, whereas the specialist | ||
| 169 | species (voles) used only overpasses. Therefore, general surveys used | 183 | species (voles) used only overpasses. Therefore, general surveys used | ||
| 170 | without species identification can underestimate the value of WCS for | 184 | without species identification can underestimate the value of WCS for | ||
| 171 | specialist small mammals, with relevant conservation implications. As | 185 | specialist small mammals, with relevant conservation implications. As | ||
| 172 | a consequence, we recommend species\u2010specific surveys of WCS | 186 | a consequence, we recommend species\u2010specific surveys of WCS | ||
| 173 | suitability for small mammals. We also suggest improving the habitat | 187 | suitability for small mammals. We also suggest improving the habitat | ||
| 174 | (or at least the cover availability) in the WCS and along the space | 188 | (or at least the cover availability) in the WCS and along the space | ||
| 175 | between them and the surrounding environments to increase WCS | 189 | between them and the surrounding environments to increase WCS | ||
| 176 | suitability for specialist species. \n Palabras clave: Mammal" | 190 | suitability for specialist species. \n Palabras clave: Mammal" | ||
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