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Predation plays a variety of important roles in structuring ecological communities. The mesopredator release effect occurs when the removal of an apex predator increases the density of a mesopredator, which in turn reduces the density of their shared prey. The mesopredator release effect can pose significant challenges for predator management and biodiversity conservation. Although several mathematical models have proposed specific circumstances that induce the mesopredator release effect, no theory has yet provided general conditions for this effect. Here, we propose a simple mathematical model to clarify the general conditions that induce the mesopredator release effect. The model predicts that the mesopredator release effect will occur when 1) the carrying capacity of the mesopredator exceeds a certain threshold, and 2) the top–down effect of the apex predator is larger on the mesopredator than on their shared prey. These conditions unify those from previous models and match the existing empirical examples. The simplicity of our theory may be useful for developing system‐specific guidelines to control the mesopredator release effect in various ecosystems. [ABSTRACT FROM AUTHOR]

Phenological resources are common across many ecological communities, and can strongly affect community dynamics. Recent field manipulation experiments in stream food chains found that seasonal timing and duration of terrestrial prey inputs affected the feeding behavior, growth, and maturation of fish predators, caused predator‐mediated indirect effects on aquatic prey, and modified trophic‐cascading effects on ecosystem processes (i.e., litter decomposition). These experiments described impacts of resource phenological changes over a few month period, but long‐term impacts of continued changes in resource phenology are unknown. Here, we develop a mathematical model to extrapolate long‐term predictions about the effects of changes in resource phenology from the results of field manipulation experiments. The model predicts that advanced timing generally decreases aquatic prey and litter processing and prolonged duration will either increase or decrease aquatic prey and litter processing depending on the total amount and pre‐disturbed timing and duration of terrestrial prey inputs. Our modeling approach clarifies that stage‐specific responses of life history processes in fish (i.e., growth, maturation, and reproduction) to phenological changes in terrestrial prey inputs mediate indirect effects on aquatic prey and litter processing. We argue that stage‐specific responses of life history processes are an integral part of the mechanisms with which to predict the consequences of phenological species interactions at the community and ecosystem levels. [ABSTRACT FROM AUTHOR]

Mutualism is a fundamental building block of ecological communities and an important driver of biotic evolution. Classic theory suggests that a pairwise two-species obligate mutualism is fragile, with a large perturbation potentially driving both mutualist populations into extinction. In nature, however, there are many cases of pairwise obligate mutualism. Such pairwise obligate mutualisms are occasionally associated with additional interactions with facultative mutualists. Here, we use a mathematical model to show that when a two-species obligate mutualism has a single additional link to a third facultative mutualist, the obligate mutualism can become permanently persistent. In the model, a facultative mutualist interacts with one of two inter-dependent obligate mutualists, and the facultative mutualist enhances the persistence not only of its directly interacting obligate mutualist, but also that of the other obligate mutualist indirectly, enabling the permanent coexistence of the three mutualist species. The effect of the facultative mutualist is strong; it can allow a three-species permanent coexistence even when two obligate mutualists by themselves are not sustainable (i.e. not locally stable). These results suggest that facultative mutualists can play a pivotal role for the persistence of obligate mutualisms, and contribute to a better understanding on the mechanisms maintaining more complex mutualistic networks of multiple species. [ABSTRACT FROM AUTHOR]

Traditionally, productivity and disturbance have been hypothesized as important determinants of food-chain length. More recently, growing empirical evidence suggests a strong role of ecosystem size. To theoretically explore the effects of basal productivity, disturbance, and ecosystem size on food-chain length, we develop and analyze a metacommunity model of intraguild predation (IGP). The model finds that, when local IGP is weak, increasing basal productivity, weakening disturbance, and increasing ecosystem size will generally increase food-chain length. When local IGP is strong, by contrast, increasing basal productivity or weakening disturbance favors intraguild predators and hinders the coexistence of intraguild predators and intraguild prey, limiting food-chain length. In contrast, increasing ecosystem size can promote coexistence even when local IGP is strong, increasing food-chain length through inserting intraguild prey and changing the degree of omnivory by intraguild predators. Intraguild prey needs to be the superior colonizer to intraguild predators for this to occur. We discuss that these theoretical predictions appear consistent with empirical patterns. [ABSTRACT FROM AUTHOR]

Local-regional species richness relationships have been used to infer relative contributions of local and regional forces to determining the richness of local communities. Although most previous research assumed competition as major local species interactions, growing empirical evidence suggests that facilitation is also an important driver of local community dynamics. Here, I explore how facilitation affects the shape of local-regional richness relationships, by incorporating local facilitation into a patch-occupancy model of metacommunity dynamics. I find that facilitation can generate local-regional richness relationships with the alternative stable states of mean local richness at intermediate to high levels of regional richness. These alternative stable states tend to occur in a metacommunity in moderately harsh environments. This result cautions against assuming that only competition can be primarily important local interactions when interpreting the shapes of local-regional richness relationships. Moreover, the possibility of alternative stable states suggests that gradual decline of regional species diversity might cause a sudden collapse of metacommunities with local facilitation. [ABSTRACT FROM AUTHOR]

1. Parasites are ubiquitous in ecosystems, but their roles in material transfer are poorly understood. Fungal parasites in freshwater ecosystems are of major importance to small heterotrophic eukaryotes and consume large phytoplankton that are resistant to zooplankton grazing. 2. To evaluate their ecosystem-level effects, we developed a simple food web model that incorporates competition between small and large phytoplankton for nutrients, zooplankton grazing on small phytoplankton, fungal parasitism on large phytoplankton and includes a newly discovered trophic link from fungal zoospores to zooplankton (F-Z link). 3. Our model demonstrates the likely occurrence of an indirect mutualism between fungi and zooplankton, in which fungal parasitism increases zooplankton production by reducing the biomass of inedible large phytoplankton. Contradicting the expectation from a previous short-term experiment that the F-Z link may benefit zooplankton, the presence of the F-Z link can reduce material transfer from phytoplankton to zooplankton because of the negative effect of the indirect mutualism. The model indicates that high growth efficiency of fungi on host tissue and their high nutrient status for zooplankton are crucial for the F-Z link to increase zooplankton production. 4. The model also indicates that the contribution of material transfer via F-Z link to zooplankton increases with nutrient availability. Our results suggest that parasitic fungi may be a key player in material transfer, especially in eutrophic ecosystems. [ABSTRACT FROM AUTHOR]

Ecologists have long struggled to explain variation in food-chain length among natural ecosystems. Food-chain length is predicted to be shorter in ecosystems subjected to greater disturbance because longer chains are theoretically less resilient to perturbation. Moreover, food-chain length is expected to be longer in larger ecosystems because increasing ecosystem size increases species richness and stabilizes predator-prey interactions, or increases total resource availability. Here we test the roles of disturbance and ecosystem size in-determining the food-chain length of terrestrial food webs on Bahamian islands. We found that disturbance affected the identity of top predators, but did not change food-chain length because alternative top predators occupied similar trophic positions. On the other hand, a 106- fold increase in ecosystem size elevated food-chain length by one trophic level. We suggest that the effect of disturbance on food-chain length is weak when alternate top predators are trophic omnivores and have similar trophic positions. This and previous work in lakes suggest that ecosystem size may be a strong determinant of food-chain length in both aquatic and terrestrial ecosystems [ABSTRACT FROM AUTHOR]

Food-chain length is a central characteristic of ecological communities because of its strong influence on community structure and ecosystem function. While recent studies have started to better clarify the relationship between food-chain length and environmental gradients such as resource availability and ecosystem size, much less progress has been made in isolating the ultimate and proximate mechanisms that determine food-chain length. Progress has been slow, in part, because research has paid little attention to the proximate changes in food web structure that must link variation in food-chain length to the ultimate dynamic mechanism. Here we outline the structural mechanisms that determine variation in food-chain length. We explore the implications of these mechanisms for understanding how changes in food-web structure influence food-chain length using both an intraguild predation community model and data from natural ecosystems. The resulting framework provides the mechanisms for linking ultimate dynamic mechanisms to variation in food-chain length. It also suggests that simple linear food-chain models may make misleading predictions about patterns of variation in food-chain length because they are unable to incorporate important structural mechanisms that alter food-web dynamics and cause non-linear shifts in food-web structure. Intraguild predation models provide a more appropriate theoretical framework for understanding food-chain length in most natural ecosystems because they accommodate all of the proximate structural mechanisms identified here. [ABSTRACT FROM AUTHOR]