The storage effect is a coexistence mechanism proposed in the ecological theory of species coexistence, which tries to explain how such a wide variety of similar species are able to coexist within the same ecological community or guild. The storage effect was originally proposed in the 1980s1 to explain coexistence in diverse communities of coral reef fish, however it has since been generalized to cover a variety of ecological communities.234 The theory proposes one way for multiple species to coexist: in a changing environment, no species can be the best under all conditions.5 Instead, each species must have a unique response to varying environmental conditions, and a way of buffering against the effects of bad years.5 The storage effect gets its name because each population "stores" the gains in good years or microhabitats (patches) to help it survive population losses in bad years or patches.1 One strength of this theory is that, unlike most coexistence mechanisms, the storage effect can be measured and quantified, with units of per-capita growth rate (offspring per adult per generation).5
The storage effect can be caused by both temporal and spatial variation. The temporal storage effect (often referred to as simply "the storage effect") occurs when species benefit from changes in year-to-year environmental patterns,1 while the spatial storage effect occurs when species benefit from variation in microhabitats across a landscape.6
For the storage effect to operate, it requires variation (i.e. fluctuations) in the environment1 and thus can be termed a "fluctuation-dependent mechanism". This variation can come from a large degree of factors, including resource availability, temperature, and predation levels. However, for the storage effect to function, this variation must change the birth, survival, or recruitment rate of species from year to year (or patch to patch).16
For competing species within the same community to coexist, they have to meet one fundamental requirement: the impact of competition from a species on itself must exceed its competitive impact on other species. In other words, intraspecific competition must exceed interspecific competition.7 For example, jackrabbits living in the same area compete for food and nesting grounds. Such competition within the same species is called intraspecific competition, which limits the growth of the species itself. Members from different species can also compete. For instance, jackrabbits and cottontail rabbits also compete for food and nesting grounds. Competition between different species is called interspecific competition, which limits the growth of other species. Stable coexistence occurs when any one species in the community limits its own growth more strongly than the growth of others.
The storage effect mixes three essential ingredients to assemble a community of competing species that fulfill the requirement. They are 1) correlation between the quality of an environment and the amount of competition experienced by a population in that environment (i.e. covariance between environment and competition), 2) differences in species response to the same environment (i.e. species-specific environmental responses), and 3) the ability of a population to diminish the impact of competition under worsening environment (i.e. buffered population growth).5 Below we describe each ingredient in detail and explain why the combination of the three leads to species coexistence.
The growth of a population can be strongly influenced by the environment it experiences. An environment consists of not only physical elements such as resource abundance, temperature, and level of physical disturbance, but also biological elements such as the abundance of natural enemies and mutualists.8 Usually organisms reproduce more in a favorable environment (i.e. either during a good year, or within a good patch), build up their population densities, and lead themselves to a high level of competition due to this increasing crowding.5 Such a trend means that higher quality environments usually correlate with a higher strength of competition experienced by the organisms in those environments. In short, a better environment results in stronger competition.5 In statistics, such correlation means that there will be a non-zero covariance between the change of population density in response to the environment and that to the competition. That is why the first ingredient is called "covariance between environment and competition".
Covariance between environment and competition suggests that organisms experience the strongest competition under their optimal environmental conditions because their populations grow most rapidly in those conditions. In nature, we often find that different species from the same community respond to the same conditions in distinctive manners. For example, plant species have different preferred levels of light and water availability, which affect their germination and physical growth rates.2 Such differences in their response to the environment, which is called "species-specific environmental response," means no two species from a community will have the same best environment in a given year or a given patch. As a result, when a species is under its optimal environmental conditions and thus experiencing the strongest intraspecific competition, other species from the same community only experience the strongest interspecific competition coming from that species, but not the strongest intraspecific competition coming from themselves.
A population can decline when environmental conditions worsen and when competition intensifies. If a species cannot limit the impact of competition in a hostile environment, its population will crash, and it will become locally extinct.1 Marvelously, in nature organisms are often able to slow down the rate of population decline in a hostile environment by alleviating the impact of competition. In so doing, they are able to set up a lower limit on the rate of their population decline.1 This phenomenon is called "buffered population growth", which occurs under a variety of situations. Under the temporal storage effect, it can be accomplished by the adults of a species having long life spans, which are relatively unaffected by environmental stressors. For example, an adult tree is unlikely to be killed by a few weeks of drought or a single night of freezing temperatures, whereas a seedling may not survive these conditions.4 Even if all seedlings are killed by bad environmental conditions, the long-lived adults are able to keep the overall population from crashing.1 Moreover, the adults usually adopt strategies such as dormancy or hibernation under a hostile environment, which make them less sensitive to competition, and allows them to buffer against the double blades of the hostile environment and competition from their rivals. For a different example, buffered population growth is attained by annual plants with a persistent seed bank.2 Thanks to these long-lived seeds, the entire population cannot be destroyed by a single bad year. Moreover, the seeds stay dormant under unfavorable environmental conditions, avoiding direct competition with rivals who are favored by the same environment, and thus diminish the impact of competition in bad years.2 There are some temporal situations in which buffered population growth is not expected to occur. Namely, when multiple generations do not overlap (such as Labord’s chameleon) or when adults have a high mortality rate (such as many aquatic insects, or some populations of the Eastern Fence Lizard 9), buffered growth does not occur. Under the spatial storage effect, buffered population growth is generally automatic, because the effects of a detrimental microhabitat will only be experienced by individuals in that area, rather than the population as a whole.6
The combined effect of (1) covariance between environment and competition, and (2) species-specific response to the environment decouple the strongest intraspecific and interspecific competition experienced by a species.5 Intraspecific competition is strongest when a species is favored by the environment, whereas interspecific competition is strongest when its rivals are favored. After this decoupling, buffered population growth limits the impact of interspecific competition when a species is not favored by the environment. As a consequence, the impact of intraspecific competition on the species favored by a particular environment exceeds that of the interspecific competition on species less favored by that environment. We see that the fundamental requirement for species coexistence is fulfilled and thus storage effect is able to maintain stable coexistence in a community of competing species.5
For species to coexist in a community, all species must be able to recover from low density.7 Not surprisingly, being a coexistence mechanism, the storage effect helps species when they become rare. It does so by making the abundant species’ effect on itself greater than its effect on the rare species.5 The difference between species’ response to environmental conditions means that a rare species’ optimal environment is not the same as its competitors. Under these conditions, the rare species will experience low levels of interspecific competition. Because the rare species itself is rare, it will experience little impact from intraspecific competition as well, even at its highest possible levels of intraspecific competition. Free from the impact of competition, the rare species is able to make gains in these good years or patches.1 Moreover, thanks to the buffered population growth, the rare species is able to survive the bad years or patches by "storing" the gains from the good years/patches. As a result, the population of any rare species is able to grow due to the storage effect.
One natural outcome from the covariance between environment and competition is that the species with very low densities will have more fluctuation in its recruitment rates than species with normal densities.10 This occurs because in good environments, species with high densities will often experience large amount of crowding by members of the same species, thus limiting the benefits of good years/patches, and making good years/patches more similar to bad years/patches. Low-density species are rarely able to cause crowding, thus allowing significantly increased fitness in good years/patches.1 Since the fluctuation in recruitment rate is an indicator of covariance between environment and competition, and since species-specific environmental response and buffered population growth can normally be assumed in nature, finding much stronger fluctuation in recruitment rates in rare and low-density species provides a strong indication that the storage effect is operating within a community.410
It is important to note that the storage effect is not a model for population growth (such as the Lotka–Volterra equation) itself, but is an effect that appears in non-additive models of population growth.5 Thus, the equations shown below will work for any arbitrary model of population growth, but will only be as accurate as the original model. The derivation below is taken from Chesson 1994.5 It is a derivation of the temporal storage effect, but is very similar to the spatial storage effect.
The fitness of an individual, as well as expected growth rate, can be measured in terms of the average number of offspring it will leave during its lifetime. This parameter, r(t), is a function of both environmental factors, e(t), and how much the organism must compete with other individuals (both of its own species, and different species), c(t). Thus,
where g is an arbitrary function for growth rate. During this article, we will at times use subscripts to represent functions of a particular species (e.g. r j(t) is the fitness of species j). It is assumed that there must be some values e* and c*, such that g(e*, c*) = 0, representing a zero-population growth equilibrium. These values need not be unique, but for every e*, there is a unique c*. For ease of calculation, we define standard parameters E(t) and C(t), such that
Both E and C represent the effect of deviations in environmental response from equilibrium. E represents the effect that varying environmental conditions (e.g. rainfall patterns, temperature, food availability, etc.) have on fitness, in the absence of abnormal competitive effects. For the storage effect to occur, the environmental response for each species must be unique (i.e. E j(t) ≠ E i(t) when j ≠ i). C(t) represents how much average fitness is lowered as a result of competition. For example, if there is more rain during a given year, E(t) will likely increase. If more plants begin to bloom, and thus compete for that rain, then C(t) will increase as well. Because e* and c* are not unique, E(t) and C(t) are not unique, and thus one should choose them as conveniently as possible. Under most conditions (see Chesson 19945), r(t) can be approximated as
γ represents the nonadditivity of growth rates. If γ = 0 (known as additivity) it means that the impact of competition on fitness does not change with the environment. If γ > 0 (superadditivity), it means that the adverse effects of competition during a bad year are relatively worse than during a good year. In other words, a population suffers more from competition in bad years than in good years. If γ < 0 (subadditivity, or buffered population growth), it means that the harm done by competition during a bad year is relatively minor when compared to a good year. In other words, the population is able to diminish the impact of competition as the environment worsens. As stated above, for the storage effect to contribute to species coexistence, we must have buffered population growth (i.e. it must be the case that γ < 0).
The long-term average of the above equation is
which, under environments with sufficient variation relative to mean effects, can be approximated as
For any effect to act as a coexistence mechanism, it must boost the average fitness of an individual when they are at below-normal population density. Otherwise, a species at low density (known as an `invader') will continue to dwindle, and this negative feedback will cause its extinction. When a species is at equilibrium (known as a `resident'), its average long-term fitness must be 0. For a species to recover from low density, its average fitness must be greater than 0. For the remainder of the text, we refer to functions of the invader with the subscript i, and to the resident with the subscript r.
A long-term average growth rate of an invader is often written as
and, ΔI, the storage effect,
In this equation, qir tells us how much the competition experienced by r affects the competition experienced by i.
We can see the biological meaning of the storage effect expressed in the mathematical form of ΔI. The first term of the expression is covariance between environment and competition (Cov(E C)), scaled by a factor representing buffered population growth (γ). The difference between the first term and the second term represents the difference in species responses to the environment between the invader and the sum of the residents, scaled by the effect each resident has on the invader (qir).5
The effect of predation on the storage effect was recently considered in a series of papers by Peter Chesson and Jessica Kuang.1112 Their work focused on a model for annual plants with seed predators, from which they reached two conclusions. First, they showed that predation can undermine the benefits of the storage effect.11 This occurs because generalist predators depress population levels by eating individuals. When this happens, there are fewer plants competing for resources. This lowers the strength of intraspecific competition relative to interspecific competition. As a result, the strength of the storage effect is weakened. In other words, when population levels are held in check by predation, rather than competition, the beneficial effects of intraspecific competition will be undermined.
Second, they found that under positive frequency dependent predation, predators can promote coexistence.12 Positive frequency dependent predation (also known as "prey switching") occurs when predators are more likely to attack a particular prey when they are common. When this occurs, death from predation most often befalls dominant species, and individuals from rare species are much more likely to survive and increase in number. When predators become specialized enough, this can promote coexistence, compensating for or even surpassing the weakening of the storage effect. Additionally, if predators are able to quickly respond to the new prey densities, this can generate a storage effect from predation.12
The first empirical study that tested the requirements of the storage effect was done by Pake and Venable,2 who looked at three desert annual plants. They experimentally manipulated density and water availability over a two-year period, and found that fitness and germination rates varied greatly from year to year, and over different environmental conditions. This shows that each species has a unique environmental response, and implied that likely there is a covariance between environment and competition. This, combined with the buffered population growth that is a product of a long-lived seed bank, showed that a temporal storage effect was probably an important factor in mediating coexistence. This study was also important, because it showed that variation in germination conditions could be a major factor promoting species coexitstence.2
The first attempt made at quantifying the temporal storage effect was by Cáceres in 1997.3 Using 30 years of water-column data from Oneida Lake, New York, she studied the effect the storage effect had on two species of plankton (Daphnia galeata mendotae and D. pulicaria). These species of plankton lay diapausing eggs which, much like the seeds of annual plants, lay dormant in the sediment for many years before hatching. Cáceres found that the size of reproductive bouts were fairly uncorrelated between the two species. She also found, in the absence of the storage effect, D. galeata mendotae would have gone extinct. She was unable to measure certain important parameters (such as the rate of egg predation), but found that her results were robust to a wide range of estimates.3
The first test of the spatial storage effect was done by Sears and Chesson 10 in the desert area east of Portal, Arizona. Using a common neighbor-removal experiment, they examined whether coexistence between two annual plants, Erodium cicutarium and Phacelia popeii, was due to the spatial storage effect or resource partitioning. The storage effect was quantified in terms of number of inflorescences (a proxy for fitness) instead of actual population growth rate. They found that E. cicutarium was able to outcompete P. popeii in many situations, and in the absence of the storage effect, would likely competitively exclude P. popeii. However, they found a very strong difference in the covariance between environment and competition, which showed that some of the most favorable areas for P. popeii (the rare species), were unfavorable to E. cicutarium (the common species). This suggests that P. popeii is able to avoid strong interspecific competition in some good patches, and that this may be enough to compensate for losses in areas favorable to E. cicutarium.10
Colleen Kelly and colleagues have used congeneric species pairs to examine storage dynamics where species similarity is a natural outcome of relatedness and not dependent on researcher-based estimates. Initial studies were of 12 species of trees coexisting in a tropical deciduous forest at the Chamela Biological Station in Jalisco, Mexico.413 For each of the 12 species they examined age structure (calculated from size and species-specific growth rate), and found that recruitment of young trees varies from year to year. Grouping the species into 6 congeneric pairs, the locally rarer species of each pair unanimously had a more irregular age distributions than the more common species. This finding strongly suggests that between closely competing tree species, the rarer species experiences stronger recruitment fluctuation than the commoner species. Such difference in recruitment fluctuation, combined with evidence of greater competitive ability in the rarer species of each pair, indicates a difference in covariance between the environment and competition between rare and common species. Since species-specific environmental response and buffered population growth can be naturally assumed, their finding strongly suggests that the storage effect operates in this tropical deciduous forest so as to maintain the coexistence between different tree species. Further work with these species has shown that the storage dynamic is a pairwise, competitive relationship, between congeneric species pairs, and possibly extending as successively nested pairs within a genus.14
Angert and colleagues demonstrated the temporal storage effect occurring in the desert annual plant community on Tumamoc Hill, Arizona.15 Previous studies1617 had shown the annual plants in that community exhibited a trade-off between growth rate (a proxy for competitive ability) and water use efficiency (a proxy for drought tolerance). As a result, some plants grew better during wet years, while others grew better during dry years. This, combined with variation in germination rates, produced an overall community average storage effect of 0.103. In other words, the storage effect is expected to help the population of any species at low density to increase, on average, by 10.3% each generation, until it recovers from low density.15
- Chesson, Peter; Warner, Robert (1981). "Environmental variability promotes coexistence in lottery competitive systems". The American Naturalist 117 (6): 923–943. doi:10.1086/283778.
- Pake, Catherine; Venable, D. Lawerance (1995). "Is coexistence of Sonoran desert annual plants mediated by temporal variability reproductive success". Ecology 76 (1): 246–261. doi:10.2307/1940646. JSTOR 1940646.
- Cáceres, Carla (1997). "Temoral variation, dormancy, and coexistence: a field test of the storage effect". Proceedings of the National Academy of Science of the United States of America 94 (17): 9171–9175. doi:10.1073/pnas.94.17.9171.
- Kelly, Colleen; Bowler, Michael (2002). "Coexistence and relative abundance in forest trees". Nature 417 (6887): 437–440. doi:10.1038/417437a. PMID 12024212.
- Chesson, Peter (1994). "Multispecies competition in variable environments". Theoretical population biology 45 (3): 227–276. doi:10.1006/tpbi.1994.1013.
- Chesson, Peter (2000). "General theory of competitive coexistence in spatially varying environments". Theoretical population biology 58 (3): 211–237. doi:10.1006/tpbi.2000.1486. PMID 11120650.
- Chesson, Peter (2000). "Mechanisms of maintenance of species diversity". Annual review of ecology and systematics 31: 343–366. doi:10.1146/annurev.ecolsys.31.1.343.
- Andrewartha, Herbert George; Birch, Charles (1954). The distribution and abundance of animals. University of Chicago Press. ISBN 0-226-02026-6.
- Tinkle, Donald; Ballinger, Royce (1972). "Sceloporus undulatus: a study of intraspecific comparative demography of a lizard". Ecology 53 (4): 570–584. doi:10.2307/1934772. JSTOR 1934772.
- Sears, Anna; Chesson, Peter (2007). "New methods for quantifying the spatial storage effect: an illustration with desert annuals". Ecology 88 (9): 2240–2247. doi:10.1890/06-0645.1. PMID 17918402.
- Kuang, Jessica; Chesson, Peter (2010). "Interacting coexistence mechanisms in annual plant communities: Frequency-dependent predation and the storage effect". Theoretical Population Biology 77 (1): 56–70. doi:10.1016/j.tpb.2009.11.002. PMID 19945475.
- Peter, Chesson; Kuang, Jessica (2010). "The storage effect due to frequency-dependent predation in multispecies plant communities". Theoretical Population Biology 78 (2): 148–164. doi:10.1016/j.tpb.2010.06.003. PMID 20600208.
- Kelly, Colleen; Bowler, Michael (2002). "Coexistence and relative abundance in forest tree species". Nature 417 (6887): 437–440. doi:10.1038/417437a. PMID 12024212.
- Kelly, Colleen; Bowler, Michael (2005). "A new application of storage dynamics: differential sensitivity, diffuse competition and temporal niches". Ecology 86 (4): 1012–1022. doi:10.1890/04-0091.
- Angert, Amy; Huxman, Travis, Chesson, Peter, and Venable, D. Lawerance (2009). "Functional tradeoffs determine species coexistence via the storage effect". Proceedings of the National Academy of Sciences of the United States of America 106 (28): 11641–11645. doi:10.1073/pnas.0904512106. PMC 2710622. PMID 19571002.
- Angert, Amy; Huxman, Travis, Barron-Gafford, Greg, Gerst, Katherine, and Venable, D. Lawerance (2009). "Linking growth strategies to long-term population dynamics in a guild of desert annuals". Journal of Ecology 95 (2): 321–331. doi:10.1111/j.1365-2745.2006.01203.x.
- Huxman, Travis; Barron-Gafford, Greg, Gerst, Katherine, Angert, Amy, Tyler, Anna, and Venable, D. Lawerance (2009). "Photosynthetic resource-use efficiency and demographic variability in desert winter annual plants". Ecology 89 (6): 1554–1563. doi:10.1890/06-2080.1. PMID 18589520.