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en Assessing road effects on bats. The role of landscape, road features and bat activity on roadkills. -
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Assessing road effects on bats. The role of landscape, road features and bat activity on roadkills.
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| 77 | "notes": "Recent studies suggest that the damage caused by roads on | 91 | "notes": "Recent studies suggest that the damage caused by roads on | ||
| 78 | bats may significantly affect bat populations. However, despite bats | 92 | bats may significantly affect bat populations. However, despite bats | ||
| 79 | being one of the most threatened groups of European vertebrates, | 93 | being one of the most threatened groups of European vertebrates, | ||
| 80 | scientific information is still lacking to effectively mitigate this | 94 | scientific information is still lacking to effectively mitigate this | ||
| 81 | effect. We daily surveyed roadkilled bats in 52 km of roads with | 95 | effect. We daily surveyed roadkilled bats in 52 km of roads with | ||
| 82 | different traffic volume in southern Portugal, between March and | 96 | different traffic volume in southern Portugal, between March and | ||
| 83 | October 2009. During the same period we also monitored bat activity in | 97 | October 2009. During the same period we also monitored bat activity in | ||
| 84 | the study area. We found 154 roadkilled bats of 11 species. | 98 | the study area. We found 154 roadkilled bats of 11 species. | ||
| 85 | Pipistrellus kuhlii and P. pygmaeus represent 64 % of total specimens | 99 | Pipistrellus kuhlii and P. pygmaeus represent 64 % of total specimens | ||
| 86 | collected. We also found threatened and poorly known species like | 100 | collected. We also found threatened and poorly known species like | ||
| 87 | Barbastella barbastellus (2), Rhinolophus ferrumequinum (1), R. | 101 | Barbastella barbastellus (2), Rhinolophus ferrumequinum (1), R. | ||
| 88 | hipposideros (5), Miniopterus shreibersii (1) and Nyctalus leisleri | 102 | hipposideros (5), Miniopterus shreibersii (1) and Nyctalus leisleri | ||
| 89 | (1). A peak of mortality occurred in late summer with 67% of bats | 103 | (1). A peak of mortality occurred in late summer with 67% of bats | ||
| 90 | being killed between 15 of July and 15 of September. The males were | 104 | being killed between 15 of July and 15 of September. The males were | ||
| 91 | killed more often than females, except in June when this pattern was | 105 | killed more often than females, except in June when this pattern was | ||
| 92 | inverted. The mortality of young was recorded only from June onwards | 106 | inverted. The mortality of young was recorded only from June onwards | ||
| 93 | and was a small percentage of total kills (approx. 16%). The | 107 | and was a small percentage of total kills (approx. 16%). The | ||
| 94 | relationship between bat fatalities and different types of explanatory | 108 | relationship between bat fatalities and different types of explanatory | ||
| 95 | variables (landscape, road characteristics and bat ecology) was | 109 | variables (landscape, road characteristics and bat ecology) was | ||
| 96 | assessed by generalized linear model (GLM) and variance partition | 110 | assessed by generalized linear model (GLM) and variance partition | ||
| 97 | techniques. Overall, landscape features explained about 37% variance | 111 | techniques. Overall, landscape features explained about 37% variance | ||
| 98 | (pure+joint effects) in bat mortality and were the most important of | 112 | (pure+joint effects) in bat mortality and were the most important of | ||
| 99 | the three variable sets analyzed. Nevertheless, bat activity, traffic | 113 | the three variable sets analyzed. Nevertheless, bat activity, traffic | ||
| 100 | and the proximity to known roosts also had a significant influence on | 114 | and the proximity to known roosts also had a significant influence on | ||
| 101 | mortality. The results have shown an increase in mortality in road | 115 | mortality. The results have shown an increase in mortality in road | ||
| 102 | sectors crossing high quality habitat (forests, streams and pond | 116 | sectors crossing high quality habitat (forests, streams and pond | ||
| 103 | vicinity); near bat roosts and core activity areas; and on high | 117 | vicinity); near bat roosts and core activity areas; and on high | ||
| 104 | traffic roads. The importance of these findings for the management and | 118 | traffic roads. The importance of these findings for the management and | ||
| 105 | implementation of effective mitigation measures of bat roadkills are | 119 | implementation of effective mitigation measures of bat roadkills are | ||
| 106 | discussed in this communication.", | 120 | discussed in this communication.", | ||
| 107 | "notes_translated": { | 121 | "notes_translated": { | ||
| 108 | "en": "Recent studies suggest that the damage caused by roads on | 122 | "en": "Recent studies suggest that the damage caused by roads on | ||
| 109 | bats may significantly affect bat populations. However, despite bats | 123 | bats may significantly affect bat populations. However, despite bats | ||
| 110 | being one of the most threatened groups of European vertebrates, | 124 | being one of the most threatened groups of European vertebrates, | ||
| 111 | scientific information is still lacking to effectively mitigate this | 125 | scientific information is still lacking to effectively mitigate this | ||
| 112 | effect. We daily surveyed roadkilled bats in 52 km of roads with | 126 | effect. We daily surveyed roadkilled bats in 52 km of roads with | ||
| 113 | different traffic volume in southern Portugal, between March and | 127 | different traffic volume in southern Portugal, between March and | ||
| 114 | October 2009. During the same period we also monitored bat activity in | 128 | October 2009. During the same period we also monitored bat activity in | ||
| 115 | the study area. We found 154 roadkilled bats of 11 species. | 129 | the study area. We found 154 roadkilled bats of 11 species. | ||
| 116 | Pipistrellus kuhlii and P. pygmaeus represent 64 % of total specimens | 130 | Pipistrellus kuhlii and P. pygmaeus represent 64 % of total specimens | ||
| 117 | collected. We also found threatened and poorly known species like | 131 | collected. We also found threatened and poorly known species like | ||
| 118 | Barbastella barbastellus (2), Rhinolophus ferrumequinum (1), R. | 132 | Barbastella barbastellus (2), Rhinolophus ferrumequinum (1), R. | ||
| 119 | hipposideros (5), Miniopterus shreibersii (1) and Nyctalus leisleri | 133 | hipposideros (5), Miniopterus shreibersii (1) and Nyctalus leisleri | ||
| 120 | (1). A peak of mortality occurred in late summer with 67% of bats | 134 | (1). A peak of mortality occurred in late summer with 67% of bats | ||
| 121 | being killed between 15 of July and 15 of September. The males were | 135 | being killed between 15 of July and 15 of September. The males were | ||
| 122 | killed more often than females, except in June when this pattern was | 136 | killed more often than females, except in June when this pattern was | ||
| 123 | inverted. The mortality of young was recorded only from June onwards | 137 | inverted. The mortality of young was recorded only from June onwards | ||
| 124 | and was a small percentage of total kills (approx. 16%). The | 138 | and was a small percentage of total kills (approx. 16%). The | ||
| 125 | relationship between bat fatalities and different types of explanatory | 139 | relationship between bat fatalities and different types of explanatory | ||
| 126 | variables (landscape, road characteristics and bat ecology) was | 140 | variables (landscape, road characteristics and bat ecology) was | ||
| 127 | assessed by generalized linear model (GLM) and variance partition | 141 | assessed by generalized linear model (GLM) and variance partition | ||
| 128 | techniques. Overall, landscape features explained about 37% variance | 142 | techniques. Overall, landscape features explained about 37% variance | ||
| 129 | (pure+joint effects) in bat mortality and were the most important of | 143 | (pure+joint effects) in bat mortality and were the most important of | ||
| 130 | the three variable sets analyzed. Nevertheless, bat activity, traffic | 144 | the three variable sets analyzed. Nevertheless, bat activity, traffic | ||
| 131 | and the proximity to known roosts also had a significant influence on | 145 | and the proximity to known roosts also had a significant influence on | ||
| 132 | mortality. The results have shown an increase in mortality in road | 146 | mortality. The results have shown an increase in mortality in road | ||
| 133 | sectors crossing high quality habitat (forests, streams and pond | 147 | sectors crossing high quality habitat (forests, streams and pond | ||
| 134 | vicinity); near bat roosts and core activity areas; and on high | 148 | vicinity); near bat roosts and core activity areas; and on high | ||
| 135 | traffic roads. The importance of these findings for the management | 149 | traffic roads. The importance of these findings for the management | ||
| 136 | and\nimplementation of effective mitigation measures of bat roadkills | 150 | and\nimplementation of effective mitigation measures of bat roadkills | ||
| 137 | are discussed in this communication.", | 151 | are discussed in this communication.", | ||
| 138 | "es": "Recent studies suggest that the damage caused by roads on | 152 | "es": "Recent studies suggest that the damage caused by roads on | ||
| 139 | bats may significantly affect bat populations. However, despite bats | 153 | bats may significantly affect bat populations. However, despite bats | ||
| 140 | being one of the most threatened groups of European vertebrates, | 154 | being one of the most threatened groups of European vertebrates, | ||
| 141 | scientific information is still lacking to effectively mitigate this | 155 | scientific information is still lacking to effectively mitigate this | ||
| 142 | effect. We daily surveyed roadkilled bats in 52 km of roads with | 156 | effect. We daily surveyed roadkilled bats in 52 km of roads with | ||
| 143 | different traffic volume in southern Portugal, between March and | 157 | different traffic volume in southern Portugal, between March and | ||
| 144 | October 2009. During the same period we also monitored bat activity in | 158 | October 2009. During the same period we also monitored bat activity in | ||
| 145 | the study area. We found 154 roadkilled bats of 11 species. | 159 | the study area. We found 154 roadkilled bats of 11 species. | ||
| 146 | Pipistrellus kuhlii and P. pygmaeus represent 64 % of total specimens | 160 | Pipistrellus kuhlii and P. pygmaeus represent 64 % of total specimens | ||
| 147 | collected. We also found threatened and poorly known species like | 161 | collected. We also found threatened and poorly known species like | ||
| 148 | Barbastella barbastellus (2), Rhinolophus ferrumequinum (1), R. | 162 | Barbastella barbastellus (2), Rhinolophus ferrumequinum (1), R. | ||
| 149 | hipposideros (5), Miniopterus shreibersii (1) and Nyctalus leisleri | 163 | hipposideros (5), Miniopterus shreibersii (1) and Nyctalus leisleri | ||
| 150 | (1). A peak of mortality occurred in late summer with 67% of bats | 164 | (1). A peak of mortality occurred in late summer with 67% of bats | ||
| 151 | being killed between 15 of July and 15 of September. The males were | 165 | being killed between 15 of July and 15 of September. The males were | ||
| 152 | killed more often than females, except in June when this pattern was | 166 | killed more often than females, except in June when this pattern was | ||
| 153 | inverted. The mortality of young was recorded only from June onwards | 167 | inverted. The mortality of young was recorded only from June onwards | ||
| 154 | and was a small percentage of total kills (approx. 16%). The | 168 | and was a small percentage of total kills (approx. 16%). The | ||
| 155 | relationship between bat fatalities and different types of explanatory | 169 | relationship between bat fatalities and different types of explanatory | ||
| 156 | variables (landscape, road characteristics and bat ecology) was | 170 | variables (landscape, road characteristics and bat ecology) was | ||
| 157 | assessed by generalized linear model (GLM) and variance partition | 171 | assessed by generalized linear model (GLM) and variance partition | ||
| 158 | techniques. Overall, landscape features explained about 37% variance | 172 | techniques. Overall, landscape features explained about 37% variance | ||
| 159 | (pure+joint effects) in bat mortality and were the most important of | 173 | (pure+joint effects) in bat mortality and were the most important of | ||
| 160 | the three variable sets analyzed. Nevertheless, bat activity, traffic | 174 | the three variable sets analyzed. Nevertheless, bat activity, traffic | ||
| 161 | and the proximity to known roosts also had a significant influence on | 175 | and the proximity to known roosts also had a significant influence on | ||
| 162 | mortality. The results have shown an increase in mortality in road | 176 | mortality. The results have shown an increase in mortality in road | ||
| 163 | sectors crossing high quality habitat (forests, streams and pond | 177 | sectors crossing high quality habitat (forests, streams and pond | ||
| 164 | vicinity); near bat roosts and core activity areas; and on high | 178 | vicinity); near bat roosts and core activity areas; and on high | ||
| 165 | traffic roads. The importance of these findings for the management and | 179 | traffic roads. The importance of these findings for the management and | ||
| 166 | implementation of effective mitigation measures of bat roadkills are | 180 | implementation of effective mitigation measures of bat roadkills are | ||
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