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Allee effect

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145:. A population exhibiting a weak Allee effect will possess a reduced per capita growth rate (directly related to individual fitness of the population) at lower population density or size. However, even at this low population size or density, the population will always exhibit a positive per capita growth rate. Meanwhile, a population exhibiting a strong Allee effect will have a critical population size or density under which the population growth rate becomes negative. Therefore, when the population density or size hits a number below this threshold, the population will be destined for extinction without any further aid. A strong Allee effect is often easier to demonstrate empirically using time series data, as one can pinpoint the population size or density at which per capita growth rate becomes negative. 240:
desirable than common species, prices for rare species can exceed high harvest costs. This phenomenon can create an "anthropogenic" Allee effect where rare species go extinct but common species are sustainably harvested. The anthropogenic Allee effect has become a standard approach for conceptualizing the threat of economic markets on endangered species. However, the original theory was posited using a one dimensional analysis of a two dimensional model. It turns out that a two dimensional analysis yields an Allee curve in human exploiter and biological population space and that this curve separating species destined to extinction vs persistence can be complicated. Even very high population sizes can potentially pass through the originally proposed Allee thresholds on predestined paths to extinction.
122: 285:). The Florida panther experienced a genetic bottleneck in the early 1990s where the population was reduced to ≈25 adult individuals. This reduction in genetic diversity was correlated with defects that include lower sperm quality, abnormal testosterone levels, cowlicks, and kinked tails. In response, a genetic rescue plan was put in motion and several female pumas from Texas were introduced into the Florida population. This action quickly led to the reduction in the prevalence of the defects previously associated with inbreeding depression. Although the timescale for this inbreeding depression is larger than of those more immediate Allee effects, it has significant implications on the long-term persistence of a species. 113:
cooperative hunting and the ability to more easily find mates, both influenced by population density, are component Allee effects, as they influence individual fitness of the population. At low population density, these component Allee effects would add up to produce an overall demographic Allee effect (increased fitness with higher population density). When population density reaches a high number, negative density dependence often offsets the component Allee effects through resource competition, thus erasing the demographic Allee effect. Allee effects might occur even at high population density for some species.
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colonization front simultaneously reduces the speed of colonization and enables a diversity of genes coming from the core of the population to remain on the front. The Allee effect also affects the spatial distribution of diversity. Whereas spatio-temporal models which do not include an Allee effect lead to a vertical pattern of genetic diversity (i.e., a strongly structured spatial distribution of genetic fractions), those including an Allee effect lead to a "horizontal pattern" of genetic diversity (i.e., an absence of genetic differentiation in space).
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increase the risk of population extinction. Whether or not demographic stochasticity can be considered a part of Allee effect is somewhat contentious however. The most current definition of Allee effect considers the correlation between population density and mean individual fitness. Therefore, random variation resulting from birth and death events would not be considered part of Allee effect as the increased risk of extinction is not a consequence of the changing fates of individuals within the population.
2515: 273:). While evolutionary theory states that expressed deleterious alleles should be purged through natural selection, purging would be most efficient only at eliminating alleles that are highly detrimental or harmful. Mildly deleterious alleles such as those that act later in life would be less likely to be removed by natural selection, and conversely, newly acquired beneficial mutations are more likely to be lost by random chance in smaller genetic pools than larger ones. 67:
1950s, a time when the field of ecology was heavily focused on the role of competition among and within species. The classical view of population dynamics stated that due to competition for resources, a population will experience a reduced overall growth rate at higher density and increased growth rate at lower density. In other words, individuals in a population would be better off when there are fewer individuals around due to a limited amount of resources (see
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individuals in the species. Examples of such cooperative behaviors include better mate finding, environmental conditioning, and group defense against predators. As these mechanisms are more-easily observable in the field, they tend to be more commonly associated with the Allee effect concept. Nevertheless, mechanisms of Allee effect that are less conspicuous such as
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Another possible benefit of aggregation is to protect against predation by group anti-predator behavior. Many species exhibit higher rates of predator vigilance behavior per individual at lower density. This increased vigilance might result in less time and energy spent on foraging, thus reducing the
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Environmental conditioning generally refers to the mechanism in which individuals work together in order to improve their immediate or future environment for the benefit of the species. This alteration could involve changes in both abiotic (temperature, turbulence, etc.) or biotic (toxins, hormones,
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The distinction between the two terms lies on the scale of the Allee effect: the presence of a demographic Allee effect suggests the presence of at least one component Allee effect, while the presence of a component Allee effect does not necessarily result in a demographic Allee effect. For example,
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Allee effects are classified by the nature of density dependence at low densities. If the population shrinks for low densities, there is a strong Allee effect. If the proliferation rate is positive and increasing then there is a weak Allee effect. The null hypothesis is that proliferation rates are
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If the sub-populations are subject to different environmental variations (i.e. separated enough that a disaster could occur at one sub-population site without affecting the other sub-populations) but still allow individuals to travel between sub-populations, then the individual sub-populations are
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Classic economic theory predicts that human exploitation of a population is unlikely to result in species extinction because the escalating costs to find the last few individuals will exceed the fixed price one achieves by selling the individuals on the market. However, when rare species are more
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Recent results based on spatio-temporal models show that the Allee effect can also promote genetic diversity in expanding populations. These results counteract commonly held notions that the Allee effect possesses net adverse consequences. Reducing the growth rate of the individuals ahead of the
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Although numerous ecological mechanisms for Allee effects exist, the list of most commonly cited facilitative behaviors that contribute to Allee effects in the literature include: mate limitation, cooperative defense, cooperative feeding, and environmental conditioning. While these behaviors are
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have a greater survival rate when there are more individuals within the tank. This led him to conclude that aggregation can improve the survival rate of individuals, and that cooperation may be crucial in the overall evolution of social structure. The term "Allee principle" was introduced in the
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Meanwhile, when demographic stochasticity results in fluctuations of sex ratios, it arguably reduces the mean individual fitness as population declines. For example, a fluctuation in small population that causes a scarcity in one sex would in turn limit the access of mates for the opposite sex,
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Demographic stochasticity refers to variability in population growth arising from sampling random births and deaths in a population of finite size. In small populations, demographic stochasticity will decrease the population growth rate, causing an effect similar to the Allee effect, which will
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of the population is detrimental to the population and increases extinction risk for the total population. In this case, the species receives none of the benefits of a small sub-population (loss of the sub-population is not catastrophic to the species as a whole) and all of the disadvantages
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present a potential case of such component Allee effects, where the density of spawning individuals can affect the survivability of the following generations. Spawning salmon carry marine nutrients they acquired from the ocean as they migrate to freshwater streams to reproduce, which in turn
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Due to its definition as the positive correlation between population density and average fitness, the mechanisms for which an Allee effect arises are therefore inherently tied to survival and reproduction. In general, these Allee effect mechanisms arise from cooperation or facilitation among
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Although the long-term population persistence of several species with low genetic variation has recently prompted debate on the generality of inbreeding depression, there are various empirical evidences for genetic Allee effects. One such case was observed in the endangered
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fertilize the surrounding habitat when they die, thus creating a more suitable habitat for the juveniles that would hatch in the following months. While compelling, this case of environmental conditioning by salmon has not been rigorously supported by empirical evidence.
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The generally accepted definition of Allee effect is positive density dependence, or the positive correlation between population density and individual fitness. It is sometimes referred to as "undercrowding" and it is analogous (or even considered synonymous by some) to
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is low. Individuals within a species often require the assistance of another individual for more than simple reproductive reasons in order to persist. The most obvious example of this is observed in animals that hunt for prey or defend against predators as a group.
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Mate limitation refers to the difficulty of finding a compatible and receptive mate for sexual reproduction at lower population size or density. This is generally a problem encountered by species that utilize passive reproduction and possess low mobility, such as
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After dividing both sides of the equation by the population size N, in the logistic growth the left hand side of the equation represents the per capita population growth rate, which is dependent on the population size N, and decreases with increasing
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throughout the population. Genetic variation within a species could range from beneficial to detrimental. Nevertheless, in a smaller sized gene pool, there is a higher chance of a stochastic event in which deleterious alleles become fixed
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classified in separate categories, they can overlap and tend to be context dependent (will operate only under certain conditions – for example, cooperative defense will only be useful when there are predators or competitors present).
252:'s role in the evolutionary potential of a species, this could in turn result in an observable Allee effect. As a species' population becomes smaller, its gene pool will be reduced in size as well. One possible outcome from this 678: 895:
more likely to go extinct than the total population. In the case of a catastrophic event decreasing numbers at a sub-population, individuals from another sub-population site may be able to repopulate the area.
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Clumping results due to individuals aggregating in response to: local habitat or landscape differences, daily and seasonal weather changes, reproductive processes, or as the result of social attractions.
608: 881: 183:, plants and sessile invertebrates. For example, wind-pollinated plants would have a lower fitness in sparse populations due to the lower likelihood of pollen successfully landing on a conspecific. 314:
Demographic and mathematical studies demonstrate that the existence of an Allee effect can reduce the speed of range expansion of a population and can even prevent biological invasions.
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Holden, Matthew H.; McDonald-Madden, Eve (2017-09-21). "High prices for rare species can drive large populations extinct: the anthropogenic Allee effect revisited".
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Tobin PC, Whitmire SL, Johnson DN, Bjørnstad ON, Liebhold AM (2007). "Invasion speed is affected by geographic variation in the strength of Allee effects".
809:{\displaystyle {\frac {\partial N}{\partial t}}=D{\frac {\partial ^{2}N}{\partial x^{2}}}+rN\left({\frac {N}{A}}-1\right)\left(1-{\frac {N}{K}}\right),} 2857: 1670: 1240:
Mooring MS, Fitzpatrick TA, Nishihira TT, Reisig DD (2004). Hall (ed.). "Vigilance, predation risk, and the Allee effect in desert bighorn sheep".
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throughout the entire range of population sizes. In contrast, when there is an Allee effect the per-capita growth rate increases with increasing
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If all sub-populations are subject to the same environmental variations (i.e. if a disaster affected one, it would affect them all) then
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Bessa-Gomes C, Legendre S, Clobert J (2004). "Allee effects, mating systems and the extinction risk in populations with two sexes".
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Courchamp, Franck; Angulo, Elena; Rivalan, Philippe; Hall, Richard J.; Signoret, Laetitia; Bull, Leigh; Meinard, Yves (2006-11-28).
3388: 204:. The confusion effect that this herding behavior would have on predators will be more effective when more individuals are present. 2546: 2309: 2238: 835: 3861: 3589: 2726: 1332:
spp.) runs and consumer fitness: growth and energy storage in stream-dwelling salmonids increase with salmon spawner density".
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Spatio-temporal models can take Allee effect into account as well. A simple example is given by the reaction-diffusion model
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decreasing the fitness of the individuals within the population. This type of Allee effect will likely be more prevalent in
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Certain species also require group foraging in order to survive. As an example, species that hunt in packs, such as the
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Clutton-Brock TH, Gaynor D, McIlrath GM, MacColl AD, Kansky R, Chadwick P, Manser M, Skinner JD, Brotherton PN (1999).
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Allee WC, Bowen E (1932). "Studies in animal aggregations: mass protection against colloidal silver among goldfishes".
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Johnson, WE; Onorato, DP; Roelke, MW; Land, ED; Cunningham, M; Belden, RC; McBride, R; Jansen, D; et al. (2010).
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Although the concept of Allee effect had no title at the time, it was first described in the 1930s by its namesake,
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Engen S, Lande R, Saether BE (2003). "Demographic stochasticity and Allee effects in populations with two sexes".
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fitness of an individual living in smaller groups. One striking example of such shared vigilance is exhibited by
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and increased vulnerability to environmental instability) and the population would survive better unfragmented.
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is the positive relationship between any measurable component of individual fitness and population density. The
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Johnson DM, Liebhold AM, Tobin PC, Bjørnstad ON (2006). "Allee effects and pulsed invasion by the gypsy moth".
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The distinction between the two terms is based on whether or not the population in question exhibits a
93:. Listed below are a few significant subcategories of the Allee effect used in the ecology literature. 4352: 3964: 3856: 3714: 3699: 3694: 3373: 3085: 2570: 2541: 2441: 2379: 2333: 2302: 1922: 71:). However, the concept of the Allee effect introduced the idea that the reverse holds true when the 2868: 891:
When a population is made up of small sub-populations additional factors to the Allee effect arise.
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Frankham R (1996). "Relationship of genetic variation to population size in wildlife- a review".
503: 471: 439: 2195: 4332: 4276: 4211: 4074: 4009: 3944: 3506: 3294: 3002: 2982: 2822: 2482: 2355: 1763:(November 1998). "Demographic Stochasticity and Allee Effect on a Scale with Isotropic Noise". 426:{\displaystyle {\frac {dN}{dt}}=-rN\left(1-{\frac {N}{A}}\right)\left(1-{\frac {N}{K}}\right),} 196:. Meanwhile, other species move in synchrony to confuse and avoid predators such as schools of 41: 1717:
Lande R (1998). "Demographic stochasticity and Allee effect on a scale with isotropic noise".
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is the positive relationship between the overall individual fitness and population density.
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Berec L, Angulo E, Courchamp F (2007). "Multiple Allee effects and population management".
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Kramer AM, Dennis B, Liebhold AM, Drake JM (2009). "The evidence for Allee effects".
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A simple mathematical example of an Allee effect is given by the cubic growth model.
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Declines in population size can result in a loss of genetic diversity, and owing to
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Lewis MA, Kareiva P (1993). "Allee dynamics and the spread of invading organisms".
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Rinella DJ, Wipfli MS, Stricker CA, Heintz RA, Rinella MJ (2012). "Pacific salmon (
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Stephens PA, Sutherland WJ, Freckleton RP (1999). "What is the Allee effect?".
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Marine conservation biology: the science of maintaining the sea's biodiversity
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is a demographic Allee effect with a critical population size or density. The
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is a demographic Allee effect without a critical population size or density.
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is a reduction in fitness of the species through the process of
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Lande, Russell; Engen, Steinar; SÆther, Bernt-Erik (2003).
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Stochastic Population Dynamics in Ecology and Conservation
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Allee WC, Emerson AE, Park O, Park T, Schmidt KP (1949).
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Stephens, PA, Sutherland, WJ and Freckleton, RP (1999).
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Davis HG, Taylor CM, Lambrinos JG, Strong DR (2004).
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where the population has a negative growth rate for
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(2004). 1285:Journal of Animal Ecology 1100:10.1007/s10144-009-0152-6 289:Demographic stochasticity 4343:Ecological stoichiometry 4308:Alternative stable state 2722:Self-propelled particles 2305:. Retrieved 19 May 2008. 2289:. Retrieved 19 May 2008. 1927:Mathematical Biosciences 534:logistic growth equation 107:demographic Allee effect 4187:Ontogenetic niche shift 4050:Ideal free distribution 3960:Ecological facilitation 3710:Malthusian growth model 3680:Consumer-resource model 3537:Paradox of the plankton 3502:Energy systems language 3222:Chemoorganoheterotrophy 3189:Optimal foraging theory 3164:Heterotrophic nutrition 2803:Collective intelligence 2669:Ant colony optimization 2145:10.1073/pnas.1201695109 1630:10.1126/science.1192891 1208:10.1073/pnas.0405230101 1011:Fundamentals of Ecology 4333:Ecological forecasting 4277:Marginal value theorem 4075:Landscape epidemiology 4010:Cross-boundary subsidy 3945:Biological interaction 3295:Microbial intelligence 2983:Green world hypothesis 2823:Microbial intelligence 2483:Shoaling and schooling 1908:10.1006/tpbi.1993.1007 996:10.1002/jez.1400610202 877: 810: 604: 526: 494: 462: 427: 127: 103:component Allee effect 48:History and background 42:population growth rate 4338:Ecological humanities 4237:Ecological energetics 4182:Niche differentiation 4045:Habitat fragmentation 3813:Ecological extinction 3760:Small population size 3512:Feed conversion ratio 3492:Ecological succession 3424:San Francisco Estuary 3338:Ecological efficiency 3280:Microbial cooperation 2275:Berryman, AA (1997). 2178:Essentials of Ecology 1181:Spartina alterniflora 878: 828:diffusion coefficient 811: 646:= critical point; and 605: 527: 495: 463: 428: 266:deleterious mutations 262:inbreeding depression 156:inbreeding depression 124: 4363:Evolutionary ecology 4328:Ecological footprint 4323:Ecological economics 4247:Ecological threshold 4242:Ecological indicator 4112:Source–sink dynamics 4065:Land change modeling 4060:Insular biogeography 3912:Species distribution 3651:Modelling ecosystems 3310:Microbial metabolism 3149:Intraguild predation 2938:Biogeochemical cycle 2904:Modelling ecosystems 2843:Spatial organization 2808:Decentralised system 2646:Sea turtle migration 2500:Swarming (honey bee) 2328:University of Oxford 1497:Conservation Biology 907:depression, loss of 836: 679: 542: 504: 472: 440: 333: 166:Ecological mechanism 4443:Population dynamics 4413:Theoretical ecology 4388:Natural environment 4252:Ecosystem diversity 4222:Ecological collapse 4212:Bateman's principle 4167:Limiting similarity 4080:Landscape limnology 3902:Species homogeneity 3740:Population modeling 3735:Population dynamics 3552:Trophic state index 2818:Group size measures 2380:Biological swarming 2136:2012PNAS..109.8828R 2033:10.1038/nature05242 2025:2006Natur.444..361J 1974:2007EcolL..10...36T 1923:van den Driessche P 1900:1993TPBio..43..141L 1865:2003Ecol...84.2378E 1830:2004EcolL...7..802B 1731:1998Oikos..83..353L 1622:2010Sci...329.1641J 1616:(5999): 1641–1645. 1581:2010AnCon..13..448R 1569:Animal Conservation 1509:1996ConBi..10.1500F 1458:2017JThBi.429..170H 1346:2012CJFAS..69Q..73R 1297:1999JAnEc..68..672C 1199:2004PNAS..10113804D 1193:(38): 13804–13807. 1138:2007TEcoE..22..185B 1092:2009PopEc..51..341K 1038:1999Oikos..87..185S 988:1932JEZ....61..185A 322:Mathematical models 283:Puma concolor coryi 209:Cooperative feeding 188:Cooperative defense 132:strong Allee effect 35:(often measured as 23:is a phenomenon in 4424:Outline of ecology 4373:Industrial ecology 4368:Functional ecology 4232:Ecological deficit 4177:Niche construction 4140:Ecosystem engineer 3917:Species–area curve 3838:Introduced species 3653:: Other components 3585:Deimatic behaviour 3487:Ecological network 3419:North Pacific Gyre 3404:hydrothermal vents 3343:Ecological pyramid 3290:Microbial food web 3101:Primary production 3046:Foundation species 2833:Predator satiation 2694:Swarm (simulation) 2689:Swarm intelligence 2664:Agent-based models 2495:Swarming behaviour 1279:Suricata suricatta 1080:Population Ecology 873: 806: 620:= population size; 600: 522: 490: 458: 423: 254:genetic bottleneck 244:Genetic mechanisms 128: 89:" in the field of 73:population density 60:Warder Clyde Allee 54:Warder Clyde Allee 4430: 4429: 4313:Balance of nature 4070:Landscape ecology 3955:Community ecology 3897:Species diversity 3833:Indicator species 3828:Gradient analysis 3705:Logistic function 3613: 3612: 3570:Animal coloration 3547:Trophic mutualism 3285:Microbial ecology 3076:Photoheterotrophs 3061:Myco-heterotrophy 2973:Ecosystem ecology 2958:Carrying capacity 2923:Abiotic component 2866: 2865: 2853:Military swarming 2798:Animal navigation 2717:Collective motion 2704:Collective motion 2571:reverse migration 2505:Swarming motility 2261:978-1-55963-662-9 2019:(7117): 361–363. 1677:. pp. 1–24. 1354:10.1139/f2011-133 960:978-0-19-956755-3 909:genetic diversity 866: 796: 764: 740: 700: 638:carrying capacity 593: 563: 413: 387: 354: 250:genetic variation 214:African wild dogs 136:weak Allee effect 4460: 4130:Ecological niche 4102:selection theory 3922:Umbrella species 3907:Species richness 3843:Invasive species 3823:Flagship species 3730:Population cycle 3725:Overexploitation 3690:Ecological yield 3640: 3633: 3626: 3617: 3616: 3522:Mesotrophic soil 3462:Climax community 3394:Marine food webs 3333:Biomagnification 3134:Chemoorganotroph 2988:Keystone species 2948:Biotic component 2893: 2886: 2879: 2870: 2869: 2679:Crowd simulation 2656:Swarm algorithms 2627:Insect migration 2532:Animal migration 2524:Animal migration 2517: 2442:Mobbing behavior 2365: 2358: 2351: 2342: 2341: 2265: 2254:. Island Press. 2242: 2236: 2228: 2211: 2210: 2208: 2207: 2191: 2185: 2174: 2168: 2167: 2157: 2147: 2115: 2106: 2105: 2071: 2062: 2053: 2052: 2008: 2002: 2001: 1957: 1951: 1950: 1918: 1912: 1911: 1883: 1877: 1876: 1859:(9): 2378–2386. 1848: 1842: 1841: 1813: 1807: 1806: 1757: 1751: 1750: 1714: 1708: 1707: 1705: 1704: 1695:. Archived from 1666: 1660: 1659: 1641: 1601: 1595: 1594: 1592: 1563:Reed DH (2010). 1560: 1554: 1553: 1535: 1529: 1528: 1503:(6): 1500–1508. 1492: 1486: 1485: 1451: 1431: 1420: 1419: 1409: 1391: 1367: 1358: 1357: 1325: 1319: 1318: 1308: 1272: 1266: 1265: 1237: 1231: 1230: 1220: 1210: 1174: 1168: 1167: 1157: 1121: 1112: 1111: 1075: 1066: 1065: 1021: 1015: 1014: 1009:Odum EP (1953). 1006: 1000: 999: 971: 965: 964: 946: 885:Laplace operator 883:one-dimensional 882: 880: 879: 874: 872: 867: 865: 864: 863: 850: 849: 840: 815: 813: 812: 807: 802: 798: 797: 789: 776: 772: 765: 757: 741: 739: 738: 737: 724: 720: 719: 709: 701: 699: 691: 683: 609: 607: 606: 601: 599: 595: 594: 586: 564: 562: 554: 546: 531: 529: 528: 523: 499: 497: 496: 491: 467: 465: 464: 459: 432: 430: 429: 424: 419: 415: 414: 406: 393: 389: 388: 380: 355: 353: 345: 337: 91:fishery sciences 4468: 4467: 4463: 4462: 4461: 4459: 4458: 4457: 4433: 4432: 4431: 4426: 4417: 4403:Systems ecology 4291: 4262:Extinction debt 4227:Ecological debt 4217:Bioluminescence 4198: 4191: 4160:marine habitats 4135:Ecological trap 4116: 3996: 3989: 3932: 3926: 3882:Rapoport's rule 3877:Priority effect 3818:Endemic species 3786: 3745:Population size 3661: 3654: 3644: 3614: 3609: 3562: 3556: 3542:Trophic cascade 3452:Bioaccumulation 3435: 3362: 3319: 3241: 3208: 3105: 3017: 2978:Ecosystem model 2911: 2897: 2867: 2862: 2781: 2743: 2698: 2650: 2518: 2509: 2374: 2369: 2272: 2262: 2230: 2229: 2219: 2217:Further reading 2214: 2205: 2203: 2192: 2188: 2175: 2171: 2130:(23): 8828–33. 2116: 2109: 2069: 2063: 2056: 2009: 2005: 1962:Ecology Letters 1958: 1954: 1919: 1915: 1884: 1880: 1873:10.1890/02-0123 1849: 1845: 1818:Ecology Letters 1814: 1810: 1779:10.2307/3546849 1758: 1754: 1739:10.2307/3546849 1715: 1711: 1702: 1700: 1693: 1667: 1663: 1602: 1598: 1561: 1557: 1550: 1536: 1532: 1493: 1489: 1432: 1423: 1368: 1361: 1326: 1322: 1273: 1269: 1238: 1234: 1175: 1171: 1122: 1115: 1076: 1069: 1046:10.2307/3547011 1022: 1018: 1007: 1003: 972: 968: 961: 947: 930: 926: 917: 871: 859: 855: 851: 845: 841: 839: 837: 834: 833: 788: 781: 777: 756: 755: 751: 733: 729: 725: 715: 711: 710: 708: 692: 684: 682: 680: 677: 676: 585: 578: 574: 555: 547: 545: 543: 540: 539: 505: 502: 501: 473: 470: 469: 441: 438: 437: 405: 398: 394: 379: 372: 368: 346: 338: 336: 334: 331: 330: 324: 312: 291: 279:Florida panther 246: 237: 175:Mate limitation 168: 151: 119: 99: 82: 69:logistic growth 56: 50: 29:population size 17: 12: 11: 5: 4466: 4456: 4455: 4450: 4445: 4428: 4427: 4422: 4419: 4418: 4416: 4415: 4410: 4405: 4400: 4395: 4390: 4385: 4383:Microecosystem 4380: 4375: 4370: 4365: 4360: 4355: 4350: 4345: 4340: 4335: 4330: 4325: 4320: 4315: 4310: 4305: 4299: 4297: 4293: 4292: 4290: 4289: 4284: 4282:Thorson's rule 4279: 4274: 4269: 4264: 4259: 4254: 4249: 4244: 4239: 4234: 4229: 4224: 4219: 4214: 4209: 4207:Assembly rules 4203: 4201: 4193: 4192: 4190: 4189: 4184: 4179: 4174: 4169: 4164: 4163: 4162: 4152: 4147: 4142: 4137: 4132: 4126: 4124: 4118: 4117: 4115: 4114: 4109: 4104: 4092: 4090:Patch dynamics 4087: 4085:Metapopulation 4082: 4077: 4072: 4067: 4062: 4057: 4052: 4047: 4042: 4037: 4032: 4027: 4022: 4017: 4012: 4007: 4001: 3999: 3991: 3990: 3988: 3987: 3982: 3980:Storage effect 3977: 3972: 3967: 3962: 3957: 3952: 3947: 3942: 3936: 3934: 3928: 3927: 3925: 3924: 3919: 3914: 3909: 3904: 3899: 3894: 3889: 3884: 3879: 3874: 3869: 3864: 3862:Neutral theory 3859: 3854: 3849: 3847:Native species 3840: 3835: 3830: 3825: 3820: 3815: 3810: 3805: 3800: 3794: 3792: 3788: 3787: 3785: 3784: 3779: 3778: 3777: 3772: 3762: 3757: 3752: 3747: 3742: 3737: 3732: 3727: 3722: 3720:Overpopulation 3717: 3712: 3707: 3702: 3697: 3692: 3687: 3682: 3677: 3672: 3666: 3664: 3656: 3655: 3643: 3642: 3635: 3628: 3620: 3611: 3610: 3608: 3607: 3602: 3597: 3592: 3587: 3582: 3577: 3572: 3566: 3564: 3558: 3557: 3555: 3554: 3549: 3544: 3539: 3534: 3529: 3527:Nutrient cycle 3524: 3519: 3517:Feeding frenzy 3514: 3509: 3504: 3499: 3497:Energy quality 3494: 3489: 3484: 3479: 3474: 3469: 3464: 3459: 3457:Cascade effect 3454: 3449: 3443: 3441: 3437: 3436: 3434: 3433: 3432: 3431: 3426: 3421: 3416: 3411: 3406: 3401: 3391: 3386: 3381: 3376: 3370: 3368: 3364: 3363: 3361: 3360: 3355: 3350: 3345: 3340: 3335: 3329: 3327: 3321: 3320: 3318: 3317: 3312: 3307: 3302: 3300:Microbial loop 3297: 3292: 3287: 3282: 3277: 3272: 3267: 3265:Lithoautotroph 3262: 3257: 3251: 3249: 3247:Microorganisms 3243: 3242: 3240: 3239: 3234: 3229: 3224: 3218: 3216: 3210: 3209: 3207: 3206: 3204:Prey switching 3201: 3196: 3191: 3186: 3181: 3176: 3171: 3166: 3161: 3156: 3151: 3146: 3141: 3136: 3131: 3126: 3121: 3115: 3113: 3107: 3106: 3104: 3103: 3098: 3093: 3088: 3083: 3081:Photosynthesis 3078: 3073: 3068: 3063: 3058: 3053: 3048: 3043: 3038: 3036:Chemosynthesis 3033: 3027: 3025: 3019: 3018: 3016: 3015: 3010: 3005: 3000: 2995: 2990: 2985: 2980: 2975: 2970: 2965: 2960: 2955: 2950: 2945: 2940: 2935: 2930: 2928:Abiotic stress 2925: 2919: 2917: 2913: 2912: 2896: 2895: 2888: 2881: 2873: 2864: 2863: 2861: 2860: 2855: 2850: 2845: 2840: 2838:Quorum sensing 2835: 2830: 2825: 2820: 2815: 2810: 2805: 2800: 2795: 2789: 2787: 2786:Related topics 2783: 2782: 2780: 2779: 2774: 2772:Swarm robotics 2769: 2764: 2759: 2753: 2751: 2749:Swarm robotics 2745: 2744: 2742: 2741: 2736: 2731: 2730: 2729: 2719: 2714: 2708: 2706: 2700: 2699: 2697: 2696: 2691: 2686: 2681: 2676: 2671: 2666: 2660: 2658: 2652: 2651: 2649: 2648: 2643: 2642: 2641: 2640: 2639: 2624: 2623: 2622: 2617: 2607: 2606: 2605: 2600: 2595: 2590: 2583:Fish migration 2580: 2578:Cell migration 2575: 2574: 2573: 2568: 2561:Bird migration 2558: 2557: 2556: 2554:coded wire tag 2551: 2550: 2549: 2539: 2528: 2526: 2520: 2519: 2512: 2510: 2508: 2507: 2502: 2497: 2492: 2491: 2490: 2480: 2479: 2478: 2473: 2463: 2462: 2461: 2451: 2450: 2449: 2447:feeding frenzy 2439: 2434: 2429: 2428: 2427: 2417: 2416: 2415: 2410: 2400: 2395: 2390: 2384: 2382: 2376: 2375: 2368: 2367: 2360: 2353: 2345: 2339: 2338: 2331: 2306: 2290: 2271: 2270:External links 2268: 2267: 2266: 2260: 2243: 2218: 2215: 2213: 2212: 2200:Ecology Theory 2186: 2169: 2107: 2080:(2): 453–473. 2054: 2003: 1952: 1933:(2): 221–247. 1913: 1894:(2): 141–158. 1878: 1843: 1824:(9): 802–812. 1808: 1752: 1725:(2): 353–358. 1709: 1691: 1661: 1596: 1575:(5): 448–457. 1555: 1548: 1530: 1487: 1421: 1359: 1320: 1291:(4): 672–683. 1267: 1248:(3): 519–532. 1232: 1169: 1132:(4): 185–191. 1113: 1086:(3): 341–354. 1067: 1032:(1): 185–190. 1016: 1001: 982:(2): 185–207. 966: 959: 927: 925: 922: 916: 913: 889: 888: 870: 862: 858: 854: 848: 844: 831: 817: 816: 805: 801: 795: 792: 787: 784: 780: 775: 771: 768: 763: 760: 754: 750: 747: 744: 736: 732: 728: 723: 718: 714: 707: 704: 698: 695: 690: 687: 658: 657: 647: 641: 631: 621: 611: 610: 598: 592: 589: 584: 581: 577: 573: 570: 567: 561: 558: 553: 550: 521: 518: 515: 512: 509: 489: 486: 483: 480: 477: 457: 454: 451: 448: 445: 434: 433: 422: 418: 412: 409: 404: 401: 397: 392: 386: 383: 378: 375: 371: 367: 364: 361: 358: 352: 349: 344: 341: 323: 320: 311: 308: 290: 287: 245: 242: 236: 233: 232: 231: 227:Pacific salmon 222: 218: 217: 210: 206: 205: 200:and flocks of 189: 185: 184: 176: 167: 164: 150: 147: 118: 115: 98: 95: 81: 78: 52:Main article: 49: 46: 15: 9: 6: 4: 3: 2: 4465: 4454: 4451: 4449: 4446: 4444: 4441: 4440: 4438: 4425: 4420: 4414: 4411: 4409: 4408:Urban ecology 4406: 4404: 4401: 4399: 4396: 4394: 4391: 4389: 4386: 4384: 4381: 4379: 4376: 4374: 4371: 4369: 4366: 4364: 4361: 4359: 4356: 4354: 4351: 4349: 4346: 4344: 4341: 4339: 4336: 4334: 4331: 4329: 4326: 4324: 4321: 4319: 4316: 4314: 4311: 4309: 4306: 4304: 4301: 4300: 4298: 4294: 4288: 4285: 4283: 4280: 4278: 4275: 4273: 4270: 4268: 4267:Kleiber's law 4265: 4263: 4260: 4258: 4255: 4253: 4250: 4248: 4245: 4243: 4240: 4238: 4235: 4233: 4230: 4228: 4225: 4223: 4220: 4218: 4215: 4213: 4210: 4208: 4205: 4204: 4202: 4200: 4194: 4188: 4185: 4183: 4180: 4178: 4175: 4173: 4170: 4168: 4165: 4161: 4158: 4157: 4156: 4153: 4151: 4148: 4146: 4143: 4141: 4138: 4136: 4133: 4131: 4128: 4127: 4125: 4123: 4119: 4113: 4110: 4108: 4105: 4103: 4101: 4097: 4093: 4091: 4088: 4086: 4083: 4081: 4078: 4076: 4073: 4071: 4068: 4066: 4063: 4061: 4058: 4056: 4053: 4051: 4048: 4046: 4043: 4041: 4040:Foster's rule 4038: 4036: 4033: 4031: 4028: 4026: 4023: 4021: 4018: 4016: 4013: 4011: 4008: 4006: 4003: 4002: 4000: 3998: 3992: 3986: 3983: 3981: 3978: 3976: 3973: 3971: 3968: 3966: 3963: 3961: 3958: 3956: 3953: 3951: 3948: 3946: 3943: 3941: 3938: 3937: 3935: 3929: 3923: 3920: 3918: 3915: 3913: 3910: 3908: 3905: 3903: 3900: 3898: 3895: 3893: 3890: 3888: 3885: 3883: 3880: 3878: 3875: 3873: 3870: 3868: 3865: 3863: 3860: 3858: 3855: 3853: 3850: 3848: 3844: 3841: 3839: 3836: 3834: 3831: 3829: 3826: 3824: 3821: 3819: 3816: 3814: 3811: 3809: 3806: 3804: 3801: 3799: 3796: 3795: 3793: 3789: 3783: 3780: 3776: 3773: 3771: 3768: 3767: 3766: 3763: 3761: 3758: 3756: 3753: 3751: 3748: 3746: 3743: 3741: 3738: 3736: 3733: 3731: 3728: 3726: 3723: 3721: 3718: 3716: 3713: 3711: 3708: 3706: 3703: 3701: 3698: 3696: 3693: 3691: 3688: 3686: 3683: 3681: 3678: 3676: 3673: 3671: 3668: 3667: 3665: 3663: 3657: 3652: 3648: 3641: 3636: 3634: 3629: 3627: 3622: 3621: 3618: 3606: 3603: 3601: 3598: 3596: 3593: 3591: 3588: 3586: 3583: 3581: 3578: 3576: 3573: 3571: 3568: 3567: 3565: 3559: 3553: 3550: 3548: 3545: 3543: 3540: 3538: 3535: 3533: 3530: 3528: 3525: 3523: 3520: 3518: 3515: 3513: 3510: 3508: 3505: 3503: 3500: 3498: 3495: 3493: 3490: 3488: 3485: 3483: 3480: 3478: 3475: 3473: 3470: 3468: 3465: 3463: 3460: 3458: 3455: 3453: 3450: 3448: 3445: 3444: 3442: 3438: 3430: 3427: 3425: 3422: 3420: 3417: 3415: 3412: 3410: 3407: 3405: 3402: 3400: 3397: 3396: 3395: 3392: 3390: 3387: 3385: 3382: 3380: 3377: 3375: 3372: 3371: 3369: 3365: 3359: 3358:Trophic level 3356: 3354: 3351: 3349: 3346: 3344: 3341: 3339: 3336: 3334: 3331: 3330: 3328: 3326: 3322: 3316: 3315:Phage ecology 3313: 3311: 3308: 3306: 3305:Microbial mat 3303: 3301: 3298: 3296: 3293: 3291: 3288: 3286: 3283: 3281: 3278: 3276: 3273: 3271: 3268: 3266: 3263: 3261: 3260:Bacteriophage 3258: 3256: 3253: 3252: 3250: 3248: 3244: 3238: 3235: 3233: 3230: 3228: 3227:Decomposition 3225: 3223: 3220: 3219: 3217: 3215: 3211: 3205: 3202: 3200: 3197: 3195: 3192: 3190: 3187: 3185: 3182: 3180: 3177: 3175: 3174:Mesopredators 3172: 3170: 3167: 3165: 3162: 3160: 3157: 3155: 3152: 3150: 3147: 3145: 3142: 3140: 3137: 3135: 3132: 3130: 3127: 3125: 3122: 3120: 3119:Apex predator 3117: 3116: 3114: 3112: 3108: 3102: 3099: 3097: 3094: 3092: 3089: 3087: 3084: 3082: 3079: 3077: 3074: 3072: 3069: 3067: 3064: 3062: 3059: 3057: 3054: 3052: 3049: 3047: 3044: 3042: 3039: 3037: 3034: 3032: 3029: 3028: 3026: 3024: 3020: 3014: 3011: 3009: 3006: 3004: 3001: 2999: 2996: 2994: 2991: 2989: 2986: 2984: 2981: 2979: 2976: 2974: 2971: 2969: 2966: 2964: 2961: 2959: 2956: 2954: 2953:Biotic stress 2951: 2949: 2946: 2944: 2941: 2939: 2936: 2934: 2931: 2929: 2926: 2924: 2921: 2920: 2918: 2914: 2909: 2905: 2901: 2894: 2889: 2887: 2882: 2880: 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2448: 2445: 2444: 2443: 2440: 2438: 2435: 2433: 2430: 2426: 2425:herd behavior 2423: 2422: 2421: 2418: 2414: 2411: 2409: 2406: 2405: 2404: 2401: 2399: 2396: 2394: 2391: 2389: 2386: 2385: 2383: 2381: 2377: 2373: 2366: 2361: 2359: 2354: 2352: 2347: 2346: 2343: 2337: 2336: 2332: 2329: 2325: 2321: 2317: 2316: 2311: 2307: 2304: 2300: 2296: 2295: 2291: 2288: 2284: 2280: 2279: 2274: 2273: 2263: 2257: 2253: 2249: 2244: 2240: 2234: 2226: 2221: 2220: 2201: 2197: 2190: 2184: 2180: 2179: 2173: 2165: 2161: 2156: 2151: 2146: 2141: 2137: 2133: 2129: 2125: 2121: 2114: 2112: 2103: 2099: 2095: 2091: 2087: 2083: 2079: 2075: 2068: 2061: 2059: 2050: 2046: 2042: 2038: 2034: 2030: 2026: 2022: 2018: 2014: 2007: 1999: 1995: 1991: 1987: 1983: 1979: 1975: 1971: 1967: 1963: 1956: 1948: 1944: 1940: 1936: 1932: 1928: 1924: 1917: 1909: 1905: 1901: 1897: 1893: 1889: 1882: 1874: 1870: 1866: 1862: 1858: 1854: 1847: 1839: 1835: 1831: 1827: 1823: 1819: 1812: 1804: 1800: 1796: 1792: 1788: 1784: 1780: 1776: 1772: 1768: 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Index

biology
population size
fitness
per capita
population growth rate
Warder Clyde Allee
Warder Clyde Allee
goldfish
logistic growth
population density
depensation
fishery sciences

critical population size or density
inbreeding depression
sex ratio
plankton
meerkats
sardines
starlings
African wild dogs
Pacific salmon
genetic variation
genetic bottleneck
genetic drift
inbreeding depression
deleterious mutations
genetic drift
Florida panther
monogamous

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