978 resultados para Biotic interactions


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Plant secondary metabolites are a group of naturally occurring compound classes biosynthesized by differing biochemical pathways whose plant content and regulation is strongly susceptible to environmental influences and to potential herbal predators. Such abiotic and biotic factors might be specifically induced by means of various mechanisms, which create variation in the accumulation or biogenesis of secondary metabolites. Hence the dynamic aspect of bioactive compound synthesis and accumulation enables plants to communicate and react in order to overcome imminent threats. This contribution aims to review the most important mechanisms of various abiotic and biotic interactions, such as pathogenic microorganisms and herbivory, by which plants respond to exogenous influences, and will also report on time-scale variable influences on secondary metabolite profiles. Transmission of signals in plants commonly occurs by 'semiochemicals', which are comprised of terpenes, phenylpropanoids, benzenoids and other volatile compounds. Due to the important functions of volatile terpenes in communication processes of living organisms, as well as its emission susceptibility relative to exogenous influences, we also present different scenarios of concentration and emission variations. Toxic effects of plants vary depending on the level and type of secondary metabolites. In farming and cattle raising scenarios, the toxicity of plant secondary metabolites and respective concentration shifts may have severe consequences on livestock production and health, culminating in adverse effects on crop yields and/or their human consumers, or have an adverse economic impact. From a wider perspective, herbal medicines, agrochemicals or other natural products are also associated with variability in plant metabolite levels, which can impact the safety and reliable efficacy of these products. We also present typical examples of toxic plants which influence livestock production using Brazilian examples of toxicity of sapogenins and alkaloids on livestock to highlight the problem. (c) 2012 Elsevier B.V. All rights reserved.

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Habitat structure is known to influence the abundance of fishes on temperate reefs. Biotic interactions play a major role in determining the distribution and abundance of species. The significance of these forces in affecting the abundance of fishes may hinge on the presence of organisms that either create or alter habitat. On temperate reefs, for example, macroalgae are considered autogenic ecosystem engineers because they control resource availability to other species through their physical structure and provide much of the structure used by fish. On both coral and temperate reefs, small cryptic reef fishes may comprise up to half of the fish numbers and constitute a diverse community containing many specialized species. Small cryptic fishes (<100 mm total length) may be responsible for the passage of 57% of the energy flow and constitute ca. 35% of the overall reef fish biomass on coral reefs. These benthic fish exploit restricted habitats where food and shelter are obtained in, or in relation to, conditions of substrate complexity and/or restricted living space. A range of mechanisms has been proposed to account for the diversity and the abundance of small fishes: (1) lifehistory strategies that promote short generation times, (2) habitat associations and behaviour that reduce predation and (3) resource partitioning that allows small species to coexist with larger competitors. Despite their abundance and potential importance within reef systems, little is known of the community ecology of cryptic fishes. Specifically on habitat associations many theories suggested a not clear direction on this subject. My research contributes to the development of marine fish ecology by addressing the effects of habitat characteristics upon distribution of cryptobenthic fish assemblages. My focus was on the important shallow, coastal ecosystems that often serve as nursery habitat for many fish and where different type of habitat is likely to both play important roles in organism distribution and survival. My research included three related studies: (1) identification of structuring forces on cryptic fish assemblages, such as physical and biological forcing; (2) macroalgae as potential tools for cryptic fish and identification of different habitat feature that could explain cryptic fish assemblages distribution; (3) canopy formers loss: consequences on cryptic fish and relationship with benthos modifications. I found that: (1) cryptic fish assemblages differ between landward and seaward sides of coastal breakwaters in Adriatic Sea. These differences are explained by 50% of the habitat characteristics on two sides, mainly due to presence of the Codium fragile, sand and oyster assemblages. Microhabitat structure influence cryptic fish assemblages. (2) Different habitat support different cryptic fish assemblages. High heterogeneity on benthic assemblages reflect different fish assemblages. Biogenic components that explain different and diverse cryptic fish assemblages are: anemonia bed, mussel bed, macroalgal stands and Cystoseira barbata, as canopy formers. (3) Canopy forming loss is not relevant in structuring directly cryptic fish assemblages. A removal of canopy forming algae did not affect the structure of cryptic fish assemblages. Canopy formers algae on Conero cliff, does not seem to act as structuring force, probably due to its regressive status. In conclusion, cryptic fish have been shown to have species-specific associations with habitat features relating to the biological and non biological components afforded by fish. Canopy formers algae do not explain cryptic fish assemblages distribution and the results of this study and information from the literature (both from the Mediterranean Sea and elsewhere) show that there are no univocal responses of fish assemblages. Further exanimations on an non regressive status of Cystoseira canopy habitat are needed to define and evaluate the relationship between canopy formers and fish on Mediterranean sea.

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Die Verbreitung von Vögeln kann von sehr unterschiedlichen Faktoren (z.B. Habitatstruktur, Klima, Nahrungsverfügbarkeit, Evolutionsgeschichte) beeinflusst werden, die zudem auf verschiedenen räumlichen Skalen (lokal bis global) unterschiedlich wirken. In dieser Dissertation wurde die Artenvielfalt früchtefressender Vogelarten auf regionalem, kontinentalem und globalem Maßstab untersucht und getestet ob sie von Habitatstruktur (Landnutzung, Topographie, Vegetationsstruktur), Klima (Temperatur, Niederschlag, Evapotranspiration), Nahrungsressourcen (früchtetragende Baumarten), oder historischen Faktoren (biogeographische Region) bestimmt wird. Dazu wurden umfangreiche geographische Datenbanken auf verschiedenen räumlichen Skalen, d.h. auf regionalem (Kenia), kontinentalem (Afrika), und globalem (Welt) Maßstab, ausgewertet, die die Verbreitung aller Vogelarten und wichtiger Umweltfaktoren enthalten. Statistische Analysen auf globalem Maßstab zeigten, dass die Verbreitung von Früchtefressern sehr gut mit klimatischen Variablen, insbesondere aktueller Evapotranspiration und Produktivität, beschrieben werden kann. Unterschiede zwischen biogeographischen Regionen bleiben jedoch bestehen auch wenn für klimatische Unterschiede zwischen den Regionen korrigiert wird. Weiter zeigen unterschiedliche Ordnungen mit früchtefressenden Vogelarten unterschiedliche Diversifizierungsmuster. Dies deutet darauf hin, dass auch historische Faktoren, wie die Klima- und Evolutionsgeschichte, eine wichtige Rolle spielen. Analysen auf regionalem und kontinentalem Maßstab legen nahe, dass klimatische Faktoren im Wesentlichen indirekt auf die Artenvielfalt von Früchtefressern wirken, und zwar durch funktionelle Beziehungen zwischen Früchtefressern und Bäumen (z.B. trophische Interaktionen mit wichtigen Nahrungspflanzen, Vegetationsstruktur). Die Ergebnisse dieser Dissertation zeigen, dass biotische Interaktionen, direkte und indirekte klimatische Effekte, und das Zusammenwirken von Evolutionsgeschichte und heutigen Umweltbedingungen untersucht werden müssen um den Artenreichtum von Vögeln auf großem räumlichem Maßstab zu verstehen.

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Streams and riparian areas can be intricately connected via physical and biotic interactions that influence habitat conditions and supply resource subsidies between these ecosystems. Streambed characteristics such as the size of substrate particles influence the composition and the abundance of emergent aquatic insects, which can be an important resource for riparian breeding birds. We predict fine sediment abundance in small headwater streams directly affects the composition and number of emergent insects while it may indirectly affect riparian bird assemblages. Streams with abundant fine sediments that embed larger substrates should have lower emergence of large insects such as phemeroptera, Plecoptera and Trichoptera. Streams with lower emergent insect abundance are predicted to support fewer breeding birds and may lack certain bird species that specialize on aquatic insects. This study examined relationships between streambed characteristics, and emergent insects (composition, abundance and biomass), and riparian breeding birds (abundance and richness) along headwater streams of the Otter River Watershed. The stream bed habitats of seven stream reaches were characterized using longitudinal surveys. Malaise traps were deployed to sample emergent aquatic insects. Riparian breeding birds were surveyed using fixed-radius point-counts. Streams differed within a wide range of fine sediment abundances. Total emergent aquatic insect abundance increased as coverage by instream substrates increased in diameter, while bird community was unresponsive to insect or stream features. Knowledge of stream and riparian relationships is important for understanding of food webs in these ecosystems, and it is useful for riparian forest conservation and improving land-use management to reduce sediment pollution in these systems.

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Inbreeding is common in plant populations and can affect plant fitness and resistance against herbivores. These effects are likely to depend on population history. In a greenhouse experiment with plants from 17 populations of Lychnis flos-cuculi, we studied the effects of experimental inbreeding on resistance and plant fitness. Depending on the levels of past herbivory and abiotic factors at the site of plant origin, we found either inbreeding or outbreeding depression in herbivore resistance. Furthermore, when not damaged experimentally by snail herbivores, plants from populations with higher heterozygosity suffered from inbreeding depression and those from populations with lower heterozygosity suffered from outbreeding depression. These effects of inbreeding and outbreeding were not apparent under experimental snail herbivory. We conclude that inbreeding effects on resistance and plant fitness depend on population history. Moreover, herbivory can mask inbreeding effects on plant fitness. Thus, understanding inbreeding effects on plant fitness requires studying multiple populations and considering population history and biotic interactions.

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Determinants of plant establishment and invasion are a key issue in ecology and evolution. Although establishment success varies substantially among species, the importance of species traits and extrinsic factors as determinants of establishment in existing communities has remained difficult to prove in observational studies because they can be confounded and mask each other. Therefore, we conducted a large multispecies field experiment to disentangle the relative importance of extrinsic factors vs. species characteristics for the establishment success of plants in grasslands. We introduced 48 alien and 45 native plant species at different seed numbers into multiple grassland sites with or without experimental soil disturbance and related their establishment success to species traits assessed in five independent multispecies greenhouse experiments. High propagule pressure and high seed mass were the most important factors increasing establishment success in the very beginning of the experiment. However, after 3 y, propagule pressure became less important, and species traits related to biotic interactions (including herbivore resistance and responses to shading and competition) became the most important drivers of success or failure. The relative importance of different traits was environment-dependent and changed over time. Our approach of combining a multispecies introduction experiment in the field with trait data from independent multispecies experiments in the greenhouse allowed us to detect the relative importance of species traits for early establishment and provided evidence that species traits—fine-tuned by environmental factors—determine success or failure of alien and native plants in temperate grasslands.

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16S rRNA genes and transcripts of Acidobacteria were investigated in 57 grassland and forest soils of three different geographic regions. Acidobacteria contributed 9-31% of bacterial 16S rRNA genes whereas the relative abundances of the respective transcripts were 4-16%. The specific cellular 16S rRNA content (determined as molar ratio of rRNA:rRNA genes) ranged between 3 and 80, indicating a low in situ growth rate. Correlations with flagellate numbers, vascular plant diversity and soil respiration suggest that biotic interactions are important determinants of Acidobacteria 16S rRNA transcript abundances in soils. While the phylogenetic composition of Acidobacteria differed significantly between grassland and forest soils, high throughput denaturing gradient gel electrophoresis and terminal restriction fragment length polymorphism fingerprinting detected 16S rRNA transcripts of most phylotypes in situ. Partial least squares regression suggested that chemical soil conditions such as pH, total nitrogen, C:N ratio, ammonia concentrations and total phosphorus affect the composition of this active fraction of Acidobacteria. Transcript abundance for individual Acidobacteria phylotypes was found to correlate with particular physicochemical (pH, temperature, nitrogen or phosphorus) and, most notably, biological parameters (respiration rates, abundances of ciliates or amoebae, vascular plant diversity), providing culture-independent evidence for a distinct niche specialization of different Acidobacteria even from the same subdivision.

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Once seen as anomalous, facilitative interactions among plants and their importance for community structure and functioning are now widely recognized. The growing body of modelling, descriptive and experimental studies on facilitation covers a wide variety of terrestrial and aquatic systems throughout the globe. However, the lack of a general body of theory linking facilitation among different types of organisms and biomes and their responses to environmental changes prevents further advances in our knowledge regarding the evolutionary and ecological implications of facilitation in plant communities. Moreover, insights gathered from alternative lines of inquiry may substantially improve our understanding of facilitation, but these have been largely neglected thus far. Despite over 15 years of research and debate on this topic, there is no consensus on the degree to which plant–plant interactions change predictably along environmental gradients (i.e. the stress-gradient hypothesis), and this hinders our ability to predict how plant–plant interactions may affect the response of plant communities to ongoing global environmental change. The existing controversies regarding the response of plant–plant interactions across environmental gradients can be reconciled when clearly considering and determining the species-specificity of the response, the functional or individual stress type, and the scale of interest (pairwise interactions or community-level response). Here, we introduce a theoretical framework to do this, supported by multiple lines of empirical evidence. We also discuss current gaps in our knowledge regarding how plant–plant interactions change along environmental gradients. These include the existence of thresholds in the amount of species-specific stress that a benefactor can alleviate, the linearity or non-linearity of the response of pairwise interactions across distance from the ecological optimum of the beneficiary, and the need to explore further how frequent interactions among multiple species are and how they change across different environments. We review the latest advances in these topics and provide new approaches to fill current gaps in our knowledge. We also apply our theoretical framework to advance our knowledge on the evolutionary aspects of plant facilitation, and the relative importance of facilitation, in comparison with other ecological processes, for maintaining ecosystem structure, functioning and dynamics. We build links between these topics and related fields, such as ecological restoration, woody encroachment, invasion ecology, ecological modelling and biodiversity–ecosystem-functioning relationships. By identifying commonalities and insights from alternative lines of research, we further advance our understanding of facilitation and provide testable hypotheses regarding the role of (positive) biotic interactions in the maintenance of biodiversity and the response of ecological communities to ongoing environmental changes.

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Soil fauna in the extreme conditions of Antarctica consists of a few microinvertebrate species patchily distributed at different spatial scales. Populations of the prostigmatic mite Stereotydeus belli and the collembolan Gressittacantha terranova from northern Victoria Land (Antarctica) were used as models to study the effect of soil properties on microarthropod distributions. In agreement with the general assumption that the development and distribution of life in these ecosystems is mainly controlled by abiotic factors, we found that the probability of occurrence of S. belli depends on soil moisture and texture and on the sampling period (which affects the general availability of water); surprisingly, none of the analysed variables were significantly related to the G. terranova distribution. Based on our results and literature data, we propose a theoretical model that introduces biotic interactions among the major factors driving the local distribution of collembolans in Antarctic terrestrial ecosystems.

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In the near future, the marine environment is likely to be subjected to simultaneous increases in temperature and decreased pH. The potential effects of these changes on intertidal, meiofaunal assemblages were investigated using a mesocosm experiment. Artificial Substrate Units containing meiofauna from the extreme low intertidal zone were exposed for 60 days to eight experimental treatments (four replicates for each treatment) comprising four pH levels: 8.0 (ambient control), 7.7 & 7.3 (predicted changes associated with ocean acidification), and 6.7 (CO2 point-source leakage from geological storage), crossed with two temperatures: 12 °C (ambient control) and 16 °C (predicted). Community structure, measured using major meiofauna taxa was significantly affected by pH and temperature. Copepods and copepodites showed the greatest decline in abundance in response to low pH and elevated temperature. Nematodes increased in abundance in response to low pH and temperature rise, possibly caused by decreased predation and competition for food owing to the declining macrofauna density. Nematode species composition changed significantly between the different treatments, and was affected by both seawater acidification and warming. Estimated nematode species diversity, species evenness, and the maturity index, were substantially lower at 16 °C, whereas trophic diversity was slightly higher at 16 °C except at pH 6.7. This study has demonstrated that the combination of elevated levels of CO2 and ocean warming may have substantial effects on structural and functional characteristics of meiofaunal and nematode communities, and that single stressor experiments are unlikely to encompass the complexity of abiotic and biotic interactions. At the same time, ecological interactions may lead to complex community responses to pH and temperature changes in the interstitial environment.

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Increasing pCO2 (partial pressure of CO2 ) in an "acidified" ocean will affect phytoplankton community structure, but manipulation experiments with assemblages briefly acclimated to simulated future conditions may not accurately predict the long-term evolutionary shifts that could affect inter-specific competitive success. We assessed community structure changes in a natural mixed dinoflagellate bloom incubated at three pCO2 levels (230, 433, and 765 ppm) in a short-term experiment (2 weeks). The four dominant species were then isolated from each treatment into clonal cultures, and maintained at all three pCO2 levels for approximately 1 year. Periodically (4, 8, and 12 months), these pCO2 -conditioned clones were recombined into artificial communities, and allowed to compete at their conditioning pCO2 level or at higher and lower levels. The dominant species in these artificial communities of CO2 -conditioned clones differed from those in the original short-term experiment, but individual species relative abundance trends across pCO2 treatments were often similar. Specific growth rates showed no strong evidence for fitness increases attributable to conditioning pCO2 level. Although pCO2 significantly structured our experimental communities, conditioning time and biotic interactions like mixotrophy also had major roles in determining competitive outcomes. New methods of carrying out extended mixed species experiments are needed to accurately predict future long-term phytoplankton community responses to changing pCO2 .

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Recent studies have discussed the consequences of ocean acidification for bacterial processes and diversity. However, the decomposition of complex substrates in marine environments, a key part of the flow of energy in ecosystems, is largely mediated by marine fungi. Although marine fungi have frequently been reported to prefer low pH levels, this group has been neglected in ocean acidification research. We present the first investigation of direct pH effects on marine fungal abundance and community structure. In microcosm experiments repeated in 2 consecutive years, we incubated natural North Sea water for 4 wk at in situ seawater pH (8.10 and 8.26), pH 7.82 and pH 7.67. Fungal abundance was determined by colony forming unit (cfu) counts, and fungal community structure was investigated by the culture-independent fingerprint method Fungal Automated Ribosomal Intergenic Spacer Analysis (F-ARISA). Furthermore, pH at the study site was determined over a yearly cycle. Fungal cfu were on average 9 times higher at pH 7.82 and 34 times higher at pH 7.67 compared to in situ seawater pH, and we observed fungal community shifts predominantly at pH 7.67. Currently, surface seawater pH at Helgoland Roads remains >8.0 throughout the year; thus we cannot exclude that fungal responses may differ in regions regularly experiencing lower pH values. However, our results suggest that under realistic levels of ocean acidification, marine fungi will reach greater importance in marine biogeochemical cycles. The rise of this group of organisms will affect a variety of biotic interactions in the sea.

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1. The spatial distribution of individual plants within a population and the population’s genetic structure are determined by several factors, like dispersal, reproduction mode or biotic interactions. The role of interspecific interactions in shaping the spatial genetic structure of plant populations remains largely unknown. 2. Species with a common evolutionary history are known to interact more closely with each other than unrelated species due to the greater number of traits they share. We hypothesize that plant interactions may shape the fine genetic structure of closely related congeners. 3. We used spatial statistics (georeferenced design) and molecular techniques (ISSR markers) to understand how two closely related congeners, Thymus vulgaris (widespread species) and T. loscosii (narrow endemic) interact at the local scale. Specific cover, number of individuals of both study species and several community attributes were measured in a 10 × 10 m plot. 4. Both species showed similar levels of genetic variation, but differed in their spatial genetic structure. Thymus vulgaris showed spatial aggregation but no spatial genetic structure, while T. loscosii showed spatial genetic structure (positive genetic autocorrelation) at short distances. The spatial pattern of T. vulgaris’ cover showed significant dissociation with that of T. loscosii. The same was true between the spatial patterns of the cover of T. vulgaris and the abundance of T. loscosii and between the abundance of each species. Most importantly, we found a correlation between the genetic structure of T. loscosii and the abundance of T. vulgaris: T. loscosii plants were genetically more similar when they were surrounded by a similar number of T. vulgaris plants. 5. Synthesis. Our results reveal spatially complex genetic structures of both congeners at small spatial scales. The negative association among the spatial patterns of the two species and the genetic structure found for T. loscosii in relation to the abundance of T. vulgaris indicate that competition between the two species may account for the presence of adapted ecotypes of T. loscosii to the abundance of a competing congeneric species. This suggests that the presence and abundance of close congeners can influence the genetic spatial structure of plant species at fine scales.

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Muchos estudios han descrito la composición y diversidad de los bosques montanos tropicales, pero los patrones espaciales y las diferentes tipos de relaciones de estos, entre especies o entre grupos funcionales ha sido poco documentada. El presente trabajo se realizó en tres parcelas completamente censadas del bosque de la Estación Biológica “Chamusquin” (Zamora Chinchipe, Ecuador), y se plantea como objetivo principal conocer la estructura espacial y dinámica del bosque montano tropical del sur del Ecuador, así como las interacciones bióticas y limitaciones abióticas que influyen en esta dinámica, para ello se planteó cuatro objetivos de estudio que son: conocer los patrones espaciales de los gremios ecológicos dentro de la zona de estudio; conocer la influencia de la dependencia negativa de la densidad sobre dos especies de helechos arborescentes (Cyatheaceae); conocer si existen especies o grupos ecológicos acumuladoras o repulsoras de diversidad en el área de estudio; y conocer cómo influyen la diversidad filogenética y la densidad del vecindario en la incidencia de herbivoría y parasitismo sobre las fases iniciales del establecimiento forestal (brinzales) así como en la supervivencia de los mismos Como paso previo para el análisis del resto de objetivos, dentro de cada parcela se marcaron todos los individuos con DAP ≥5 cm y se tomaron sus coordenadas (X, Y). Además se tomaron datos de variables superficiales y muestras del suelo. Las especies encontradas se clasificaron de acuerdo a sus características biológicas, asignándolas a cada uno de los cuatro gremios forestales usualmente distinguidos en los bosques tropicales: tolerantes a la sombra (TS), tolerantes parciales a la sombra (TPS), pioneras de vida larga (PVL) y pioneras de vida corta (PVC). Para el estudio del primer objetivo tas se emplearon funciones K de Ripley inhomogéneas, ajustando la heterogeneidad en base a la variación espacial de las variables ambientales registradas . Los resultados demostraron que tanto la frecuencia relativa como el patrón espacial de las diferentes estrategias funcionales varían a lo largo de la sucesión y que éste además está influido por la variación ambiental. En adición, tanto el patrón espacial como la respuesta a la variación ambiental de los diferentes gremios es distinta entre adultos y juveniles. Todo ello sugiere que el ensamblaje de la diversidad en los bosque montanos andinos está controlado por procesos deterministas más que por procesos neutrales. Para responder el segundo objetivo se estudiaron los efectos de la dependencia negativa de la densidad (DND) y la heterogeneidad ambiental en las poblaciones de dos especies de helechos arborescentes abundantes, Cyathea caracasana y Alsophila engelii, y cómo estos efectos cambian a través de un gradiente sucesional. Los patrones de especies albergan información sobre procesos tales como la competencia que puede ser revelado fácilmente utilizando técnicas de análisis de patrones punto. Sin embargo, su detección puede ser difícil debido a los efectos de factores de confusión heterogeneidad del hábitat. Aquí, empleamos funciones K y funciones de correlación de par homogéneas y no homogéneas para cuantificar el cambio en el patrón espacial de diferentes clases de tamaño con un diseño de casos-controles para estudiar las asociaciones entre helechos arborescentes jóvenes y adultos. Usando estimaciones espaciales de la biomasa de los cuatro tipos de gremios ecológicos (PVC, PVL, TPS, TS) como covariables, hemos ajustado modelos de Poisson heterogéneos a los patrones de puntos de de los helechos juveniles y los adultos y hemos explorado además la existencia de dependencia del hábitat en estos patrones. Nuestro estudio reveló efectos de la DND para C. caracasana y un fuerte filtrado ambiental que subyace al patrón de A. engelii. Encontramos también que las poblaciones de adultos y juveniles de ambas especies respondieron de manera diferente a la heterogeneidad del hábitat y en la mayoría de los casos esta heterogeneidad se asoció con la distribución espacial de la biomasa de los cuatro tipos de gremios. Estos resultados muestran la eficacia de controlar los efectos de la heterogeneidad ambiental para evitar su confusión con los patrones derivados de interacciones biológicas cuando se estudia la DND y demuestran la utilidad de los mapas de covariables derivados de comunidades biológicas como resumen de la heterogeneidad ambiental. Para nuestro tercer objetivo nos centramos en explorar cómo influyen las especies más abundantes en la organización espacial de la diversidad a lo largo de un gradiente sucesional en el bosque montano del sur del Ecuador. Para ello utilizamos la función ISAR (Individual Species Area Relationship). Encontramos que la frecuencia de especies neutras, repulsoras y acumuladoras de diversidad taxonómica varía dependiendo del grado de sucesión. Además se comprobó que la mayoría de los gremios forestales se comportó de forma neutral, pero la proporción de acumuladores, aumentó al avanzar la sucesión hacia estados más maduros, lo que indica el establecimiento de fuertes procesos competitivos a medida que avanza la sucesión y la mayor importancia del papel de las especies individuales en dichos estados. Finalmente, examinamos el efecto de la vecindad taxonómica y filogenética, así como la estrategia de vida, sobre la incidencia de la herbivoría y el parasitismo en las poblaciones de brinzales de tres fragmentos forestales en una secuencia sucesional del bosque montano húmedo. Evaluamos además los efectos de herbivoría, parasitismo, estrategia de vida y diferentes indicadores de la vecindad sobre la supervivencia de los brinzales. Por último contrastamos la posible existencia de una tendencia compensatoria de la comunidad (CCT) a nivel de fragmento forestal. Nuestros análisis no consiguieron detectar una CCT pero si pusieron de manifiesto la existencia de efectos locales de dependencia negativa de la densidad. Por ejemplo, la presencia de herbivoría y parasitismo sobre los brinzales se relacionó significativamente con una menor supervivencia de estos. Por otro lado, indicadores del efecto de la vecindad como la densidad de brinzales del mismo género y el área basal de árboles vecinos del mismo género incrementaron la prevalencia de la herbivoría o el parasitismo en los brinzales. El incremento de la incidencia de la herbivoría o el parasitismo no está exclusivamente ligado a tener una vecindad taxonómicamente idéntica (vecinos de la misma especie) sino que categorías taxonómicas más laxas como el "género" o simplemente relaciones de semejanza filogenética son capaces de predecir los efectos negativos de la vecindad. Los efectos detectados variaron en los diferentes grupos funcionales distinguidos. Los resultados que hemos obtenido en este trabajo parecen indicar que el funcionamiento de las comunidades de brinzales del bosque montano tropical no difiere mucho del reportado para comunidades de plántulas en otros bosques tropicales y cumple las predicciones de la hipótesis de Janzen y Connell, aunque matizadas por la mayor resistencia de los brinzales al efecto de herbivoría y parasitismo. ABSTRACT Many studies have described the composition and diversity of tropical montane forests, but the different spatial patterns and types of relationships between species or between functional groups has been poorly documented. This work was made in three completely surveyed forest plots at Biological Station "Chamusquin" (Zamora Chinchipe, Ecuador). Our main objective was to know the spatial structure and dynamics of the tropical montane forest in southern Ecuador, as well as the biotic interactions and abiotic constraints affecting this dynamic. More specifically, we aimed to understand the spatial patterns of ecological guilds; to explore the influence of negative density dependence on two species of tree ferns (Cyatheaceae); to determine whether some species or ecological groups structure spatially plant diversity in these forests; and to test the effects of biological neighborhood on the incidence of herbivory and parasitism and on the survival of saplings. We mapped within each plot all trees with DBH ≥5 cm. Besides, surface data variables and soil samples they were taken. The species found were classified according to their biological characteristics in four forest guilds: shade-tolerant (ST), partial shade tolerant (PST), long-lived pioneer (LLP) and short-lived pioneer (SLP). To analyze the spatial patterns of the ecological guilds, we employed the inhomogeneous version of Ripley's K-function and adjusted heterogeneity surfaces based on the spatial variation of the measured environmental variables. The results showed that both the relative frequency of each functional guild as well as their spatial pattern varied throughout succession and that the spatial pattern is explained by environmental variation. In addition, both spatial pattern and the response to spatial variation of each guild varied throughout ontogeny. All in all suggest that diversity assembly in the studied forests is ruled by deterministic instead of neutral processes. We also addressed the negative effects of density dependence (NDD) and environmental heterogeneity in populations of two species of abundant tree ferns, Cyathea caracasana and Alsophila engelii, and how these effects change across a successional gradient.. Here, we used homogeneous and inhomogeneous K and pair-correlation functions to quantify the change in the spatial pattern of different size classes with a case-control design to study associations between young and adult tree ferns. Using spatial estimates of the biomass of the four types of ecological guilds (SLP, LLP, PST, ST) as co-variables, we fitted heterogeneous Poisson models to juvenile and adult tree fern point patterns and explored the existence of habitat dependence. Our study revealed NDD effects for C. caracasana and strong environmental filtering underlying the pattern of A. engelii. We found that adult and juvenile populations of both species responded differently to habitat heterogeneity and in most cases this heterogeneity was associated with the spatial distribution of biomass of the four functional tree types. These findings show the effectiveness of factoring out environmental heterogeneity to avoid confounding factors when studying NDD and demonstrate the usefulness of covariate maps derived from mapped communities. For our third objective we focused on exploring how the most abundant species influence the spatial organization of tree diversity in these forests. For this, we used the individual species-area relationship function (ISAR). We found that the proportion of accumulator, repeller and neutral species, varied depending on the degree of succession. We found also that most guilds behaved neutrally but the proportion of accumulator guilds increased as succession advanced to more mature stages. This point, to the existence of strong competitive effects mediated by individual species in these mature forests. Finally, we examined the effects of life strategies and taxonomic and phylogenetic neighborhood on the incidence of herbivory and parasitism in the communities of saplings in the same forest fragments. We evaluated also the effects of life strategies, herbivory, parasitism and some indicators of neighborhood on sapling survival. Finally we tested for the existences of a compensatory community trend at plot scale. We did not found a CCT but we found proof of local NND effects. For instance, the prevalence of herbivory and parasitism were related to lower sapling survival. On the other hand the density of con-generic saplings and the basal area of neighbor con-generic trees were related to a higher prevalence of herbivory or parasitism in the saplings. We demonstrated that the increase in the prevalence of herbivory or parasitism it s not exclusive of a conspecific neighborhood but instead larger taxonomic categories such as "genus" or simple phylogenetic relationships are also able to predict NND effects. The NND effects varied among functional guilds. Our results show that the dynamic of sapling communities in Ecuadorian montane forests is similar to seedling dynamics in other tropical forest and follows the predictions of Janzen-Connell hypothesis, although softened by the strong resilience of saplings in comparison to seedlings.

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Restoration efforts in the Mediterranean Basin have been changing from a silvicultural to an ecological restoration approach. Yet, to what extent the projects are guided by ecological restoration principles remains largely unknown. To analyse this issue, we built an on-line survey addressed to restoration practitioners. We analysed 36 restoration projects, mostly from drylands (86%). The projects used mainly soil from local sources. The need to comply with legislation was more important as a restoration motive for European Union (EU) than for non-EU countries, while public opinion and health had a greater importance in the latter. Non-EU countries relied more on non-native plant species than EU countries, thus deviating from ecological restoration guidelines. Nursery-grown plants used were mostly of local or regional provenance, whilst seeds were mostly of national provenance. Unexpected restoration results (e.g. inadequate biodiversity) were reported for 50% of the projects and restoration success was never evaluated in 22%. Long term evaluation (> 6 years) was only performed in 31% of cases, and based primarily on plant diversity and cover. The use of non-native species and species of exogenous provenances may: i) entail the loss of local genetic and functional trait diversity, critical to cope with drought, particularly under the predicted climate change scenarios, and ii) lead to unexpected competition with native species and/or negatively impact local biotic interactions. Absent or inappropriate monitoring may prevent the understanding of restoration trajectories, precluding adaptive management strategies, often crucial to create functional ecosystems able to provide ecosystem services. The overview of ecological restoration projects in the Mediterranean Basin revealed high variability among practices and highlighted the need for improved scientific assistance and information exchange, greater use of native species of local provenance, and more long-term monitoring and evaluation, including functional and ecosystem services' indicators, to improve and spread the practice of ecological restoration.