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| DOI | 10.1093/AOBPLA/PLX056 | ||||
| Año | 2017 | ||||
| Tipo | artículo de investigación |
Citas Totales
Autores Afiliación Chile
Instituciones Chile
% Participación
Internacional
Autores
Afiliación Extranjera
Instituciones
Extranjeras
Harsh environmental conditions in arid ecosystems limit seedling recruitment to microhabitats under nurse structures, such as shrubs or rocks. These structures, however, do not necessarily afford the same benefits to plants because nurse rocks provide only physical nurse effects, whereas nurse plants can provide both physical and biological nurse effects. Nevertheless, if the nurse plant is a conspecific, the benefits it provides may be outweighed by higher mortality due to negative density-dependent processes; consequently, negative density-dependence is expected to limit plants from acting as nurses to their own seedlings. The degree to which an abiotic nurse may be more beneficial than a conspecific one remains largely unexplored. Here, we examine the role and elucidate the mechanisms by which conspecific plants and rocks promote plant establishment in a hyper-arid desert. For 4 years, we examined establishment patterns of Myrcianthes coquimbensis (Myrtaceae), a threatened desert shrub that recruits solely in rock cavities and under conspecific shrubs. Specifically, we characterized these microhabitats, as well as open interspaces for comparison, and conducted germination, seed removal and seedling survival experiments. Our results revealed that conspecific shrubs and nurse rocks modified environmental conditions in similar ways; soil and air temperatures were lower, and water availability was higher than in open interspaces. We found no evidence on negative density-dependent recruitment: seed removal was lowest and seedling emergence highest under conspecific plants, moreover seedling survival probabilities were similar in rock cavities and under conspecific plants. We conclude that the probability of establishment was highest under conspecific plants than in other microhabitats, contrasting what is expected under the Janzen-Connell recruitment model. We suggest that for species living in stressful environments, population regulation may be a function of positive density-dependence and intraspecific facilitation may be a process that promotes the persistence of some plant species within a community.
| Ord. | Autor | Género | Institución - País |
|---|---|---|---|
| 1 | LOAYZA-FREIRA, ANDREA PATRICIA | Mujer |
Universidad de la Serena - Chile
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| 2 | Herrera-Madariaga, Marisol A. | Mujer |
Universidad de la Serena - Chile
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| 3 | CARVAJAL-LOPEZ, DANNY EDUARDO | Hombre |
Universidad de la Serena - Chile
Instituto de Ecologia y Biodiversidad - Chile |
| 4 | Garcia-Guzman, Patricio | Hombre |
Universidad de la Serena - Chile
Instituto de Ecologia y Biodiversidad - Chile |
| 5 | SQUEO-PORCILE, FRANCISCO ANTONIO | Hombre |
Universidad de la Serena - Chile
Instituto de Ecologia y Biodiversidad - Chile Centro de Estudios Avanzados en Zonas Aridas - Chile |
| Fuente |
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| CONICYT |
| Rufford Foundation |
| Fondo Nacional de Desarrollo Científico y Tecnológico |
| Comisión Nacional de Investigación Científica y Tecnológica |
| Institute of Ecology and Biodiversity |
| Rufford Small Grant Foundation |
| Fondecyt Initiation Grant |
| Comisión Nacional de Investigación CientÃfica y Tecnológica |
| Fondo Nacional de Desarrollo CientÃfico y Tecnológico |
| IEB |
| Conicyt doctoral fellowships |
| Institute of Ecology and Biodiversity (IEB) Chilean Millennium Initiative |
| FONDECYT Post-Doctoral Research Grant |
| Agradecimiento |
|---|
| This research was supported by grants awarded to A.P.L. from the Rufford Small Grant Foundation, a FONDECYT Post-Doctoral Research Grant (3120123), a FONDECYT Initiation Grant (11140400), the Institute of Ecology and Biodiversity (IEB) Chilean Millennium Initiative (P05-002) and CONICYT (PFB-23). M.A.H.-M. was supported by the IEB (P05-002), and D.E.C. and P.G.-G. were supported by CONICYT Doctoral fellowships (21140050 and 21120854, respectively) and the IEB (P05-002). |
| This research was supported by grants awarded to A.P.L. from the Rufford Small Grant Foundation, a FONDECYT Post-Doctoral Research Grant (3120123), a FONDECYT Initiation Grant (11140400), the Institute of Ecology and Biodiversity (IEB) Chilean Millennium Initiative (P05-002) and CONICYT (PFB-23). M.A.H.-M. was supported by the IEB (P05-002), and D.E.C. and P.G.-G. were supported by CONICYT Doctoral fellowships (21140050 and 21120854, respectively) and the IEB (P05-002). |