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| 4 | "alternate_identifier": "DOI: 10.1007/s10344-019-1285-3", | 4 | "alternate_identifier": "DOI: 10.1007/s10344-019-1285-3", | ||
| 5 | "author": "Mestre, F., Lopes, H., Pinto, T., Sousa, L.G., Mira, A. y | 5 | "author": "Mestre, F., Lopes, H., Pinto, T., Sousa, L.G., Mira, A. y | ||
| 6 | Santos, S.M.", | 6 | Santos, S.M.", | ||
| 7 | "author_name": "Mestre, F., Lopes, H., Pinto, T., Sousa, L.G., Mira, | 7 | "author_name": "Mestre, F., Lopes, H., Pinto, T., Sousa, L.G., Mira, | ||
| 8 | A. y Santos, S.M.", | 8 | A. y Santos, S.M.", | ||
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| 33 | "created": "2025-05-23", | 33 | "created": "2025-05-23", | ||
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| 36 | "name": "Mestre, F., Lopes, H., Pinto, T., Sousa, L.G., Mira, A. | 36 | "name": "Mestre, F., Lopes, H., Pinto, T., Sousa, L.G., Mira, A. | ||
| 37 | y Santos, S.M." | 37 | y Santos, S.M." | ||
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| 58 | "lineage_process_steps": [], | 58 | "lineage_process_steps": [], | ||
| 59 | "lineage_source": [ | 59 | "lineage_source": [ | ||
| 60 | "European Journal of Wildlife Research. Vol. 65", | 60 | "European Journal of Wildlife Research. Vol. 65", | ||
| 61 | "Num. 4", | 61 | "Num. 4", | ||
| 62 | "pag. 58" | 62 | "pag. 58" | ||
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| 80 | "modified": "2026-06-23", | 80 | "modified": "2026-06-23", | ||
| 81 | "name": "f963cbd5-e303-5db3-af53-00227d20e96a", | 81 | "name": "f963cbd5-e303-5db3-af53-00227d20e96a", | ||
| 82 | "notes": "Annually, roads, and their associated users, are | 82 | "notes": "Annually, roads, and their associated users, are | ||
| 83 | responsible for millions of roadkills worldwide. Mortality affects | 83 | responsible for millions of roadkills worldwide. Mortality affects | ||
| 84 | multiple taxonomic groups, but amphibians are particularly vulnerable, | 84 | multiple taxonomic groups, but amphibians are particularly vulnerable, | ||
| 85 | due to their size and underreporting. In fact, very high mortality | 85 | due to their size and underreporting. In fact, very high mortality | ||
| 86 | frequencies can occur, mostly during short periods of time, when | 86 | frequencies can occur, mostly during short periods of time, when | ||
| 87 | individuals migrate to and from reproduction areas (e.g., ponds). In | 87 | individuals migrate to and from reproduction areas (e.g., ponds). In | ||
| 88 | this study, we assess the influence of the lunar cycle on amphibian | 88 | this study, we assess the influence of the lunar cycle on amphibian | ||
| 89 | roadkills, while accounting for weather conditions. As expected, the | 89 | roadkills, while accounting for weather conditions. As expected, the | ||
| 90 | main environmental effects explaining roadkill numbers were weather | 90 | main environmental effects explaining roadkill numbers were weather | ||
| 91 | related, with increases in minimum air temperature, average relative | 91 | related, with increases in minimum air temperature, average relative | ||
| 92 | air humidity, and cumulative rainfall during the previous 24 h having | 92 | air humidity, and cumulative rainfall during the previous 24 h having | ||
| 93 | a positive effect on roadkill numbers for all studied species. | 93 | a positive effect on roadkill numbers for all studied species. | ||
| 94 | However, the lunar cycle also affected roadkills for two of the | 94 | However, the lunar cycle also affected roadkills for two of the | ||
| 95 | studied species. Darker nights had higher numbers of roadkills of | 95 | studied species. Darker nights had higher numbers of roadkills of | ||
| 96 | Pleurodeles waltl, while moonlit nights had higher numbers of | 96 | Pleurodeles waltl, while moonlit nights had higher numbers of | ||
| 97 | Salamandra salamandra. As such, these moon effects are species | 97 | Salamandra salamandra. As such, these moon effects are species | ||
| 98 | specific. Animals that are more active in moonlight may be at an | 98 | specific. Animals that are more active in moonlight may be at an | ||
| 99 | advantage if their visual acuity is better than that of their | 99 | advantage if their visual acuity is better than that of their | ||
| 100 | predators. We hypothesize that differences between species in the | 100 | predators. We hypothesize that differences between species in the | ||
| 101 | response to moonlight may be due to differences perceived in predation | 101 | response to moonlight may be due to differences perceived in predation | ||
| 102 | risk. This information should be considered when designing mitigation | 102 | risk. This information should be considered when designing mitigation | ||
| 103 | measures. Volunteer actions, for instance, can be planned and | 103 | measures. Volunteer actions, for instance, can be planned and | ||
| 104 | coordinated keeping in mind the most appropriate weather conditions | 104 | coordinated keeping in mind the most appropriate weather conditions | ||
| 105 | for the general amphibian community and specific phases of the lunar | 105 | for the general amphibian community and specific phases of the lunar | ||
| 106 | cycle for particular species.", | 106 | cycle for particular species.", | ||
| 107 | "notes_translated": { | 107 | "notes_translated": { | ||
| 108 | "en": "Annually, roads, and their associated users, are | 108 | "en": "Annually, roads, and their associated users, are | ||
| 109 | responsible for millions of roadkills worldwide. Mortality affects | 109 | responsible for millions of roadkills worldwide. Mortality affects | ||
| 110 | multiple taxonomic groups, but amphibians are particularly vulnerable, | 110 | multiple taxonomic groups, but amphibians are particularly vulnerable, | ||
| 111 | due to their size and underreporting. In fact, very high mortality | 111 | due to their size and underreporting. In fact, very high mortality | ||
| 112 | frequencies can occur, mostly during short periods of time, when | 112 | frequencies can occur, mostly during short periods of time, when | ||
| 113 | individuals migrate to and from reproduction areas (e.g., ponds). In | 113 | individuals migrate to and from reproduction areas (e.g., ponds). In | ||
| 114 | this study, we assess the influence of the lunar cycle on amphibian | 114 | this study, we assess the influence of the lunar cycle on amphibian | ||
| 115 | roadkills, while accounting for weather conditions. As expected, the | 115 | roadkills, while accounting for weather conditions. As expected, the | ||
| 116 | main environmental effects explaining roadkill numbers were weather | 116 | main environmental effects explaining roadkill numbers were weather | ||
| 117 | related, with increases in minimum air temperature, average relative | 117 | related, with increases in minimum air temperature, average relative | ||
| 118 | air humidity, and cumulative rainfall during the previous 24\u00a0h | 118 | air humidity, and cumulative rainfall during the previous 24\u00a0h | ||
| 119 | having a positive effect on roadkill numbers for all studied species. | 119 | having a positive effect on roadkill numbers for all studied species. | ||
| 120 | However, the lunar cycle also affected roadkills for two of the | 120 | However, the lunar cycle also affected roadkills for two of the | ||
| 121 | studied species. Darker nights had higher numbers of roadkills | 121 | studied species. Darker nights had higher numbers of roadkills | ||
| 122 | of\u00a0Pleurodeles waltl, while moonlit nights had higher numbers | 122 | of\u00a0Pleurodeles waltl, while moonlit nights had higher numbers | ||
| 123 | of\u00a0Salamandra salamandra. As such, these moon effects are species | 123 | of\u00a0Salamandra salamandra. As such, these moon effects are species | ||
| 124 | specific. Animals that are more active in moonlight may be at an | 124 | specific. Animals that are more active in moonlight may be at an | ||
| 125 | advantage if their visual acuity is better than that of their | 125 | advantage if their visual acuity is better than that of their | ||
| 126 | predators. We hypothesize that differences between species in the | 126 | predators. We hypothesize that differences between species in the | ||
| 127 | response to moonlight may be due to differences perceived in predation | 127 | response to moonlight may be due to differences perceived in predation | ||
| 128 | risk. This information should be considered when designing mitigation | 128 | risk. This information should be considered when designing mitigation | ||
| 129 | measures. Volunteer actions, for instance, can be planned and | 129 | measures. Volunteer actions, for instance, can be planned and | ||
| 130 | coordinated keeping in mind the most appropriate weather conditions | 130 | coordinated keeping in mind the most appropriate weather conditions | ||
| 131 | for the general amphibian community and specific phases of the lunar | 131 | for the general amphibian community and specific phases of the lunar | ||
| 132 | cycle for particular species.", | 132 | cycle for particular species.", | ||
| 133 | "es": "Annually, roads, and their associated users, are | 133 | "es": "Annually, roads, and their associated users, are | ||
| 134 | responsible for millions of roadkills worldwide. Mortality affects | 134 | responsible for millions of roadkills worldwide. Mortality affects | ||
| 135 | multiple taxonomic groups, but amphibians are particularly vulnerable, | 135 | multiple taxonomic groups, but amphibians are particularly vulnerable, | ||
| 136 | due to their size and underreporting. In fact, very high mortality | 136 | due to their size and underreporting. In fact, very high mortality | ||
| 137 | frequencies can occur, mostly during short periods of time, when | 137 | frequencies can occur, mostly during short periods of time, when | ||
| 138 | individuals migrate to and from reproduction areas (e.g., ponds). In | 138 | individuals migrate to and from reproduction areas (e.g., ponds). In | ||
| 139 | this study, we assess the influence of the lunar cycle on amphibian | 139 | this study, we assess the influence of the lunar cycle on amphibian | ||
| 140 | roadkills, while accounting for weather conditions. As expected, the | 140 | roadkills, while accounting for weather conditions. As expected, the | ||
| 141 | main environmental effects explaining roadkill numbers were weather | 141 | main environmental effects explaining roadkill numbers were weather | ||
| 142 | related, with increases in minimum air temperature, average relative | 142 | related, with increases in minimum air temperature, average relative | ||
| 143 | air humidity, and cumulative rainfall during the previous 24 h having | 143 | air humidity, and cumulative rainfall during the previous 24 h having | ||
| 144 | a positive effect on roadkill numbers for all studied species. | 144 | a positive effect on roadkill numbers for all studied species. | ||
| 145 | However, the lunar cycle also affected roadkills for two of the | 145 | However, the lunar cycle also affected roadkills for two of the | ||
| 146 | studied species. Darker nights had higher numbers of roadkills of | 146 | studied species. Darker nights had higher numbers of roadkills of | ||
| 147 | Pleurodeles waltl, while moonlit nights had higher numbers of | 147 | Pleurodeles waltl, while moonlit nights had higher numbers of | ||
| 148 | Salamandra salamandra. As such, these moon effects are species | 148 | Salamandra salamandra. As such, these moon effects are species | ||
| 149 | specific. Animals that are more active in moonlight may be at an | 149 | specific. Animals that are more active in moonlight may be at an | ||
| 150 | advantage if their visual acuity is better than that of their | 150 | advantage if their visual acuity is better than that of their | ||
| 151 | predators. We hypothesize that differences between species in the | 151 | predators. We hypothesize that differences between species in the | ||
| 152 | response to moonlight may be due to differences perceived in predation | 152 | response to moonlight may be due to differences perceived in predation | ||
| 153 | risk. This information should be considered when designing mitigation | 153 | risk. This information should be considered when designing mitigation | ||
| 154 | measures. Volunteer actions, for instance, can be planned and | 154 | measures. Volunteer actions, for instance, can be planned and | ||
| 155 | coordinated keeping in mind the most appropriate weather conditions | 155 | coordinated keeping in mind the most appropriate weather conditions | ||
| 156 | for the general amphibian community and specific phases of the lunar | 156 | for the general amphibian community and specific phases of the lunar | ||
| 157 | cycle for particular species." | 157 | cycle for particular species." | ||
| 158 | }, | 158 | }, | ||
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| 160 | "num_tags": 2, | 160 | "num_tags": 2, | ||
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| 184 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 184 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 185 | Demogr\u00e1fico", | 185 | Demogr\u00e1fico", | ||
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| 302 | "title": "Bad moon rising? The influence of the lunar cycle on | 302 | "title": "Bad moon rising? The influence of the lunar cycle on | ||
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