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en Does daily movements can predict the genetic structure of small mammal populations? -
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Does daily movements can predict the genetic structure of small mammal populations?
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| 84 | "notes": "Roads can constrain movements of individuals and | 98 | "notes": "Roads can constrain movements of individuals and | ||
| 85 | consequently gene flow across landscape. There is a consensus among | 99 | consequently gene flow across landscape. There is a consensus among | ||
| 86 | experts that some species show road surface and width avoidance | 100 | experts that some species show road surface and width avoidance | ||
| 87 | behavior. However, little attention has been paid on how spatial | 101 | behavior. However, little attention has been paid on how spatial | ||
| 88 | behavior can be translated into mortality risk and population genetic | 102 | behavior can be translated into mortality risk and population genetic | ||
| 89 | structure. With this study we examine the strength of the barrier | 103 | structure. With this study we examine the strength of the barrier | ||
| 90 | effects of different roads types (4-lane highway, 2-lane paved road | 104 | effects of different roads types (4-lane highway, 2-lane paved road | ||
| 91 | and unpaved road) on three rodent species with varying life-history | 105 | and unpaved road) on three rodent species with varying life-history | ||
| 92 | traits: water vole Arvicola sapidus, pine vole Microtus | 106 | traits: water vole Arvicola sapidus, pine vole Microtus | ||
| 93 | duodecimcostatus and algerian mouse Mus spretus. More specifically, we | 107 | duodecimcostatus and algerian mouse Mus spretus. More specifically, we | ||
| 94 | address 1) the influence of traffic on individual movements, 2) the | 108 | address 1) the influence of traffic on individual movements, 2) the | ||
| 95 | effect of road type (width/pavement) on crossing rates, 3) the annual | 109 | effect of road type (width/pavement) on crossing rates, 3) the annual | ||
| 96 | risk of mortality and 4) the genetic structure of populations on both | 110 | risk of mortality and 4) the genetic structure of populations on both | ||
| 97 | sides of the different roads. A total of 79 voles were caught in the | 111 | sides of the different roads. A total of 79 voles were caught in the | ||
| 98 | vicinity of roads and 6481 locations were recorded through radio | 112 | vicinity of roads and 6481 locations were recorded through radio | ||
| 99 | tracking. We used generalized linear mixed models to evaluate the | 113 | tracking. We used generalized linear mixed models to evaluate the | ||
| 100 | effect of traffic on individual movements, compared observed crossing | 114 | effect of traffic on individual movements, compared observed crossing | ||
| 101 | rates with simulations without roads, and used the information of | 115 | rates with simulations without roads, and used the information of | ||
| 102 | number of crossings per individual and the probability of being killed | 116 | number of crossings per individual and the probability of being killed | ||
| 103 | while crossing a road to estimate the annual mortality risk. We also | 117 | while crossing a road to estimate the annual mortality risk. We also | ||
| 104 | obtained 200 tissue samples for pine vole and Algerian mouse and | 118 | obtained 200 tissue samples for pine vole and Algerian mouse and | ||
| 105 | estimate the genetic differentiation (FST) among groups of samples on | 119 | estimate the genetic differentiation (FST) among groups of samples on | ||
| 106 | both sides of roads. As expected, paved roads function as artificial | 120 | both sides of roads. As expected, paved roads function as artificial | ||
| 107 | territorial boundaries for the three species. Traffic intensity had | 121 | territorial boundaries for the three species. Traffic intensity had | ||
| 108 | only negative influence on water vole movements. Crossing rates | 122 | only negative influence on water vole movements. Crossing rates | ||
| 109 | decrease as the road width increase and paved roads have a negative | 123 | decrease as the road width increase and paved roads have a negative | ||
| 110 | effect on individual\u2019s crossings, except for pine vole that had | 124 | effect on individual\u2019s crossings, except for pine vole that had | ||
| 111 | the highest crossing rate, and the 2-lane highway show a neutral | 125 | the highest crossing rate, and the 2-lane highway show a neutral | ||
| 112 | effect. The likelihood of being killed during a crossing event at high | 126 | effect. The likelihood of being killed during a crossing event at high | ||
| 113 | traffic highway segments for pine vole and Algerian mouse at 4-lan | 127 | traffic highway segments for pine vole and Algerian mouse at 4-lan | ||
| 114 | highways were 0.22 and 0.05, respectively. Unexpectedly, pine vole | 128 | highways were 0.22 and 0.05, respectively. Unexpectedly, pine vole | ||
| 115 | populations show genetic structure at 4-lane highways while Algerian | 129 | populations show genetic structure at 4-lane highways while Algerian | ||
| 116 | mouse populations did not show significant genetic structure for all | 130 | mouse populations did not show significant genetic structure for all | ||
| 117 | type of roads. Our study shows that daily movement patterns of small | 131 | type of roads. Our study shows that daily movement patterns of small | ||
| 118 | mammals towards roads cannot be translated on dispersal and gene flow. | 132 | mammals towards roads cannot be translated on dispersal and gene flow. | ||
| 119 | Further information is needed to understand the implications of | 133 | Further information is needed to understand the implications of | ||
| 120 | mortality risk in the viability of pine vole population occurring in | 134 | mortality risk in the viability of pine vole population occurring in | ||
| 121 | the vicinity of heavy traffic roads. We recommend that only | 135 | the vicinity of heavy traffic roads. We recommend that only | ||
| 122 | complementary studies of spatial behavior, population density and | 136 | complementary studies of spatial behavior, population density and | ||
| 123 | genetics may explain the mechanisms underlying the barrier effect of | 137 | genetics may explain the mechanisms underlying the barrier effect of | ||
| 124 | roads on wildlife.", | 138 | roads on wildlife.", | ||
| 125 | "notes_translated": { | 139 | "notes_translated": { | ||
| 126 | "en": "Roads can constrain movements of individuals and | 140 | "en": "Roads can constrain movements of individuals and | ||
| 127 | consequently gene flow across landscape. There is a consensus among | 141 | consequently gene flow across landscape. There is a consensus among | ||
| 128 | experts that some species show road surface and width avoidance | 142 | experts that some species show road surface and width avoidance | ||
| 129 | behavior. However, little attention has been paid on how spatial | 143 | behavior. However, little attention has been paid on how spatial | ||
| 130 | behavior can be translated into mortality risk and population genetic | 144 | behavior can be translated into mortality risk and population genetic | ||
| 131 | structure. With this study we examine the strength of the barrier | 145 | structure. With this study we examine the strength of the barrier | ||
| 132 | effects of different roads types (4-lane highway, 2-lane paved road | 146 | effects of different roads types (4-lane highway, 2-lane paved road | ||
| 133 | and unpaved road) on three rodent species with varying life-history | 147 | and unpaved road) on three rodent species with varying life-history | ||
| 134 | traits: water vole Arvicola sapidus, pine vole Microtus | 148 | traits: water vole Arvicola sapidus, pine vole Microtus | ||
| 135 | duodecimcostatus and algerian mouse Mus spretus. More specifically, we | 149 | duodecimcostatus and algerian mouse Mus spretus. More specifically, we | ||
| 136 | address 1) the influence of traffic on individual movements, 2) the | 150 | address 1) the influence of traffic on individual movements, 2) the | ||
| 137 | effect of road type (width/pavement) on crossing rates, 3) the annual | 151 | effect of road type (width/pavement) on crossing rates, 3) the annual | ||
| 138 | risk of mortality and 4) the genetic structure of populations on both | 152 | risk of mortality and 4) the genetic structure of populations on both | ||
| 139 | sides of the different roads. A total of 79 voles were caught in the | 153 | sides of the different roads. A total of 79 voles were caught in the | ||
| 140 | vicinity of roads and 6481 locations were recorded through radio | 154 | vicinity of roads and 6481 locations were recorded through radio | ||
| 141 | tracking. We used generalized linear mixed models to evaluate the | 155 | tracking. We used generalized linear mixed models to evaluate the | ||
| 142 | effect of traffic on individual movements, compared observed crossing | 156 | effect of traffic on individual movements, compared observed crossing | ||
| 143 | rates with simulations without roads, and used the information of | 157 | rates with simulations without roads, and used the information of | ||
| 144 | number of crossings per individual and the probability of being killed | 158 | number of crossings per individual and the probability of being killed | ||
| 145 | while crossing a road to estimate the annual mortality risk. We also | 159 | while crossing a road to estimate the annual mortality risk. We also | ||
| 146 | obtained\n200 tissue samples for pine vole and Algerian mouse and | 160 | obtained\n200 tissue samples for pine vole and Algerian mouse and | ||
| 147 | estimate the genetic differentiation (FST) among groups of samples on | 161 | estimate the genetic differentiation (FST) among groups of samples on | ||
| 148 | both sides of roads. As expected, paved roads function as artificial | 162 | both sides of roads. As expected, paved roads function as artificial | ||
| 149 | territorial boundaries for the three species. Traffic intensity had | 163 | territorial boundaries for the three species. Traffic intensity had | ||
| 150 | only negative influence on water vole movements. Crossing rates | 164 | only negative influence on water vole movements. Crossing rates | ||
| 151 | decrease as the road width increase and paved roads have a negative | 165 | decrease as the road width increase and paved roads have a negative | ||
| 152 | effect on individual\u2019s crossings, except for pine vole that had | 166 | effect on individual\u2019s crossings, except for pine vole that had | ||
| 153 | the highest crossing rate, and the 2-lane highway show a neutral | 167 | the highest crossing rate, and the 2-lane highway show a neutral | ||
| 154 | effect. The likelihood of being killed during a crossing event at high | 168 | effect. The likelihood of being killed during a crossing event at high | ||
| 155 | traffic highway segments for pine vole and Algerian mouse at 4-lan | 169 | traffic highway segments for pine vole and Algerian mouse at 4-lan | ||
| 156 | highways were 0.22 and 0.05, respectively. Unexpectedly, pine vole | 170 | highways were 0.22 and 0.05, respectively. Unexpectedly, pine vole | ||
| 157 | populations show genetic structure at 4-lane highways while Algerian | 171 | populations show genetic structure at 4-lane highways while Algerian | ||
| 158 | mouse populations did not show significant genetic structure for all | 172 | mouse populations did not show significant genetic structure for all | ||
| 159 | type of roads. Our study shows that daily movement patterns of small | 173 | type of roads. Our study shows that daily movement patterns of small | ||
| 160 | mammals towards roads cannot be translated on dispersal and gene flow. | 174 | mammals towards roads cannot be translated on dispersal and gene flow. | ||
| 161 | Further information is needed to understand the implications of | 175 | Further information is needed to understand the implications of | ||
| 162 | mortality risk in the viability of pine vole population occurring in | 176 | mortality risk in the viability of pine vole population occurring in | ||
| 163 | the vicinity of heavy traffic roads. We recommend that only | 177 | the vicinity of heavy traffic roads. We recommend that only | ||
| 164 | complementary studies of spatial behavior, population density and | 178 | complementary studies of spatial behavior, population density and | ||
| 165 | genetics may explain the mechanisms underlying the barrier effect of | 179 | genetics may explain the mechanisms underlying the barrier effect of | ||
| 166 | roads on wildlife.", | 180 | roads on wildlife.", | ||
| 167 | "es": "Roads can constrain movements of individuals and | 181 | "es": "Roads can constrain movements of individuals and | ||
| 168 | consequently gene flow across landscape. There is a consensus among | 182 | consequently gene flow across landscape. There is a consensus among | ||
| 169 | experts that some species show road surface and width avoidance | 183 | experts that some species show road surface and width avoidance | ||
| 170 | behavior. However, little attention has been paid on how spatial | 184 | behavior. However, little attention has been paid on how spatial | ||
| 171 | behavior can be translated into mortality risk and population genetic | 185 | behavior can be translated into mortality risk and population genetic | ||
| 172 | structure. With this study we examine the strength of the barrier | 186 | structure. With this study we examine the strength of the barrier | ||
| 173 | effects of different roads types (4-lane highway, 2-lane paved road | 187 | effects of different roads types (4-lane highway, 2-lane paved road | ||
| 174 | and unpaved road) on three rodent species with varying life-history | 188 | and unpaved road) on three rodent species with varying life-history | ||
| 175 | traits: water vole Arvicola sapidus, pine vole Microtus | 189 | traits: water vole Arvicola sapidus, pine vole Microtus | ||
| 176 | duodecimcostatus and algerian mouse Mus spretus. More specifically, we | 190 | duodecimcostatus and algerian mouse Mus spretus. More specifically, we | ||
| 177 | address 1) the influence of traffic on individual movements, 2) the | 191 | address 1) the influence of traffic on individual movements, 2) the | ||
| 178 | effect of road type (width/pavement) on crossing rates, 3) the annual | 192 | effect of road type (width/pavement) on crossing rates, 3) the annual | ||
| 179 | risk of mortality and 4) the genetic structure of populations on both | 193 | risk of mortality and 4) the genetic structure of populations on both | ||
| 180 | sides of the different roads. A total of 79 voles were caught in the | 194 | sides of the different roads. A total of 79 voles were caught in the | ||
| 181 | vicinity of roads and 6481 locations were recorded through radio | 195 | vicinity of roads and 6481 locations were recorded through radio | ||
| 182 | tracking. We used generalized linear mixed models to evaluate the | 196 | tracking. We used generalized linear mixed models to evaluate the | ||
| 183 | effect of traffic on individual movements, compared observed crossing | 197 | effect of traffic on individual movements, compared observed crossing | ||
| 184 | rates with simulations without roads, and used the information of | 198 | rates with simulations without roads, and used the information of | ||
| 185 | number of crossings per individual and the probability of being killed | 199 | number of crossings per individual and the probability of being killed | ||
| 186 | while crossing a road to estimate the annual mortality risk. We also | 200 | while crossing a road to estimate the annual mortality risk. We also | ||
| 187 | obtained 200 tissue samples for pine vole and Algerian mouse and | 201 | obtained 200 tissue samples for pine vole and Algerian mouse and | ||
| 188 | estimate the genetic differentiation (FST) among groups of samples on | 202 | estimate the genetic differentiation (FST) among groups of samples on | ||
| 189 | both sides of roads. As expected, paved roads function as artificial | 203 | both sides of roads. As expected, paved roads function as artificial | ||
| 190 | territorial boundaries for the three species. Traffic intensity had | 204 | territorial boundaries for the three species. Traffic intensity had | ||
| 191 | only negative influence on water vole movements. Crossing rates | 205 | only negative influence on water vole movements. Crossing rates | ||
| 192 | decrease as the road width increase and paved roads have a negative | 206 | decrease as the road width increase and paved roads have a negative | ||
| 193 | effect on individual\u2019s crossings, except for pine vole that had | 207 | effect on individual\u2019s crossings, except for pine vole that had | ||
| 194 | the highest crossing rate, and the 2-lane highway show a neutral | 208 | the highest crossing rate, and the 2-lane highway show a neutral | ||
| 195 | effect. The likelihood of being killed during a crossing event at high | 209 | effect. The likelihood of being killed during a crossing event at high | ||
| 196 | traffic highway segments for pine vole and Algerian mouse at 4-lan | 210 | traffic highway segments for pine vole and Algerian mouse at 4-lan | ||
| 197 | highways were 0.22 and 0.05, respectively. Unexpectedly, pine vole | 211 | highways were 0.22 and 0.05, respectively. Unexpectedly, pine vole | ||
| 198 | populations show genetic structure at 4-lane highways while Algerian | 212 | populations show genetic structure at 4-lane highways while Algerian | ||
| 199 | mouse populations did not show significant genetic structure for all | 213 | mouse populations did not show significant genetic structure for all | ||
| 200 | type of roads. Our study shows that daily movement patterns of small | 214 | type of roads. Our study shows that daily movement patterns of small | ||
| 201 | mammals towards roads cannot be translated on dispersal and gene flow. | 215 | mammals towards roads cannot be translated on dispersal and gene flow. | ||
| 202 | Further information is needed to understand the implications of | 216 | Further information is needed to understand the implications of | ||
| 203 | mortality risk in the viability of pine vole population occurring in | 217 | mortality risk in the viability of pine vole population occurring in | ||
| 204 | the vicinity of heavy traffic roads. We recommend that only | 218 | the vicinity of heavy traffic roads. We recommend that only | ||
| 205 | complementary studies of spatial behavior, population density and | 219 | complementary studies of spatial behavior, population density and | ||
| 206 | genetics may explain the mechanisms underlying the barrier effect of | 220 | genetics may explain the mechanisms underlying the barrier effect of | ||
| 207 | roads on wildlife." | 221 | roads on wildlife." | ||
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