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) en The effects of small fish presence on a species-poor community dominated by omnivores: Example of a size-based trophic cascade
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| 90 | "notes": "Omnivory is important in determining species interactions | 100 | "notes": "Omnivory is important in determining species interactions | ||
| 91 | and weakening possible trophic cascade effects. The present study is | 101 | and weakening possible trophic cascade effects. The present study is | ||
| 92 | focused on determining if an indirect effect of fish presence (trophic | 102 | focused on determining if an indirect effect of fish presence (trophic | ||
| 93 | cascade effect) can be observed regardless of a high abundance of | 103 | cascade effect) can be observed regardless of a high abundance of | ||
| 94 | omnivores. With this aim a field experiment was carried out in a | 104 | omnivores. With this aim a field experiment was carried out in a | ||
| 95 | Mediterranean salt marsh. The natural top predator of these systems is | 105 | Mediterranean salt marsh. The natural top predator of these systems is | ||
| 96 | a small and endangered fish, the Iberian toothcarp (Aphanius iberus). | 106 | a small and endangered fish, the Iberian toothcarp (Aphanius iberus). | ||
| 97 | We wanted to assess if the presence of this fish could trigger a | 107 | We wanted to assess if the presence of this fish could trigger a | ||
| 98 | tro\u0002phic cascade in the aquatic community. Six mesocosms were | 108 | tro\u0002phic cascade in the aquatic community. Six mesocosms were | ||
| 99 | installed in a salt marsh lagoon without A. iberus presence, for two | 109 | installed in a salt marsh lagoon without A. iberus presence, for two | ||
| 100 | months. Twenty adult females of A. iberus were added to three | 110 | months. Twenty adult females of A. iberus were added to three | ||
| 101 | mesocosms (fish treatment), while the other three were used as control | 111 | mesocosms (fish treatment), while the other three were used as control | ||
| 102 | (without any A. iberus addition). Physical and chemical water | 112 | (without any A. iberus addition). Physical and chemical water | ||
| 103 | characteristics, as well as aquatic invertebrate samples (from | 113 | characteristics, as well as aquatic invertebrate samples (from | ||
| 104 | bacteria to amphipoda, the largest organisms detected beside fish) | 114 | bacteria to amphipoda, the largest organisms detected beside fish) | ||
| 105 | were collected at the begining and the end of the experiment. To | 115 | were collected at the begining and the end of the experiment. To | ||
| 106 | assess the trophic po\u0002sition of organisms, stable isotope | 116 | assess the trophic po\u0002sition of organisms, stable isotope | ||
| 107 | analyses were used (13C and 15N). Our results show that the presence | 117 | analyses were used (13C and 15N). Our results show that the presence | ||
| 108 | of A. iberus produces a trophic cascade even though only two trophic | 118 | of A. iberus produces a trophic cascade even though only two trophic | ||
| 109 | levels were differentiated by the stable iso\u0002tope analysis. Body | 119 | levels were differentiated by the stable iso\u0002tope analysis. Body | ||
| 110 | size appears to be determinant, since trophic interactions observed | 120 | size appears to be determinant, since trophic interactions observed | ||
| 111 | within the food web were mainly body-size dependent. Moreover, an | 121 | within the food web were mainly body-size dependent. Moreover, an | ||
| 112 | unexpected positive but weak effect of A. iberus on macro\u0002phyte | 122 | unexpected positive but weak effect of A. iberus on macro\u0002phyte | ||
| 113 | biomass was observed, caused probably by the decrease of small | 123 | biomass was observed, caused probably by the decrease of small | ||
| 114 | phytoplankton abundance. This effect may suppose an advantage for A. | 124 | phytoplankton abundance. This effect may suppose an advantage for A. | ||
| 115 | iberus, since macrophytes provide refuge and a food supply for this | 125 | iberus, since macrophytes provide refuge and a food supply for this | ||
| 116 | small fish.", | 126 | small fish.", | ||
| 117 | "notes_translated": { | 127 | "notes_translated": { | ||
| 118 | "es": "Omnivory is important in determining species interactions | 128 | "es": "Omnivory is important in determining species interactions | ||
| 119 | and weakening possible trophic cascade effects. The present study is | 129 | and weakening possible trophic cascade effects. The present study is | ||
| 120 | focused on determining if an indirect effect of fish presence (trophic | 130 | focused on determining if an indirect effect of fish presence (trophic | ||
| 121 | cascade effect) can be observed regardless of a high abundance of | 131 | cascade effect) can be observed regardless of a high abundance of | ||
| 122 | omnivores. With this aim a field experiment was carried out in a | 132 | omnivores. With this aim a field experiment was carried out in a | ||
| 123 | Mediterranean salt marsh. The natural top predator of these systems is | 133 | Mediterranean salt marsh. The natural top predator of these systems is | ||
| 124 | a small and endangered fish, the Iberian toothcarp (Aphanius iberus). | 134 | a small and endangered fish, the Iberian toothcarp (Aphanius iberus). | ||
| 125 | We wanted to assess if the presence of this fish could trigger a | 135 | We wanted to assess if the presence of this fish could trigger a | ||
| 126 | tro\u0002phic cascade in the aquatic community. Six mesocosms were | 136 | tro\u0002phic cascade in the aquatic community. Six mesocosms were | ||
| 127 | installed in a salt marsh lagoon without A. iberus presence, for two | 137 | installed in a salt marsh lagoon without A. iberus presence, for two | ||
| 128 | months. Twenty adult females of A. iberus were added to three | 138 | months. Twenty adult females of A. iberus were added to three | ||
| 129 | mesocosms (fish treatment), while the other three were used as control | 139 | mesocosms (fish treatment), while the other three were used as control | ||
| 130 | (without any A. iberus addition). Physical and chemical water | 140 | (without any A. iberus addition). Physical and chemical water | ||
| 131 | characteristics, as well as aquatic invertebrate samples (from | 141 | characteristics, as well as aquatic invertebrate samples (from | ||
| 132 | bacteria to amphipoda, the largest organisms detected beside fish) | 142 | bacteria to amphipoda, the largest organisms detected beside fish) | ||
| 133 | were collected at the begining and the end of the experiment. To | 143 | were collected at the begining and the end of the experiment. To | ||
| 134 | assess the trophic po\u0002sition of organisms, stable isotope | 144 | assess the trophic po\u0002sition of organisms, stable isotope | ||
| 135 | analyses were used (13C and 15N). Our results show that the presence | 145 | analyses were used (13C and 15N). Our results show that the presence | ||
| 136 | of A. iberus produces a trophic cascade even though only two trophic | 146 | of A. iberus produces a trophic cascade even though only two trophic | ||
| 137 | levels were differentiated by the stable iso\u0002tope analysis. Body | 147 | levels were differentiated by the stable iso\u0002tope analysis. Body | ||
| 138 | size appears to be determinant, since trophic interactions observed | 148 | size appears to be determinant, since trophic interactions observed | ||
| 139 | within the food web were mainly body-size dependent. Moreover, an | 149 | within the food web were mainly body-size dependent. Moreover, an | ||
| 140 | unexpected positive but weak effect of A. iberus on macro\u0002phyte | 150 | unexpected positive but weak effect of A. iberus on macro\u0002phyte | ||
| 141 | biomass was observed, caused probably by the decrease of small | 151 | biomass was observed, caused probably by the decrease of small | ||
| 142 | phytoplankton abundance. This effect may suppose an advantage for A. | 152 | phytoplankton abundance. This effect may suppose an advantage for A. | ||
| 143 | iberus, since macrophytes provide refuge and a food supply for this | 153 | iberus, since macrophytes provide refuge and a food supply for this | ||
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