Nordic Society Oikos What Is the Allee Effect? Author(s): P. A. Stephens, W. J. Sutherland, R. P. Freckleton Source: Oikos, Vol. 87, No. 1 (Oct., 1999), pp. 185-190 Published by: Blackwell Publishing on behalf of Nordic Society Oikos Stable URL: http://www.jstor.org/stable/3547011 Accessed: 31/03/2009 09:26 Your use of the JSTOR archive indicates your acceptance of JSTOR's Terms and Conditions of Use, available at http://www.jstor.org/page/info/about/policies/terms.jsp. JSTOR's Terms and Conditions of Use provides, in part, that unless you have obtained prior permission, you may not download an entire issue of a journal or multiple copies of articles, and you may use content in the JSTOR archive only for your personal, non-commercial use. Please contact the publisher regarding any further use of this work. Publisher contact information may be obtained at http://www.jstor.org/action/showPublisher?publisherCode=black. 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Blackwell Publishing and Nordic Society Oikos are collaborating with JSTOR to digitize, preserve and extend access to Oikos. http://www.jstor.org FORUM FORUM FORUM FORUMis intendedfor new ideasor newwaysof interpreting It existinginformation. currentthinkingon providesa chancefor suggestinghypothesesand for challenging Formal ecologicalissues.A lighterprose,designedto attractreaders,will be permitted. shouldbe concise research andall contributions reports,albeitshort,willnot be accepted, witha relatively A summary is not required. shortlist of references. What is the Allee effect? P. A. Stephens, W. J. Sutherlandand R. P. Freckleton,School of Biological Sciences, Univ. of East Anglia, Norwich,UK NR4 7TJ ([email protected]). W. C. Allee broughtattentionto the possibilityof a positive relationshipbetweenaspectsof fitnessand populationsize over fifty years ago. This phenomenon, frequentlytermedthe Allee effect,has beenthe focusof increasedinterestoverthe past two decades in the light of concernsover conservationand the problemsof rarity.Use of the termsuffersfromthe absenceof a clear definitionhowever,withthe resultthat Allee effectsare frequentlythoughtto involveonly a narrowrangeof phenomena andare oftenoverlookedaltogether.We proposea definitionfor the effectandattemptto resolvethe majorissuesunderlying the confusionsurrounding this term. It is recognisedthat individualsof many species may benefit from the presence of conspecifics(Fig. 1), a conceptbroadlyreferredto as the Allee effect afterthe pioneeringwork of W. C. Allee (Allee 1931, 1938,Allee et al. 1949). Unfortunately,however,the concept suffers from widespreadconfusionand misuse.It has been interpretedsolely as the difficultyin findingmates at low densities(Myerset al. 1995,Amarasekare1998),is explained variously as a reduction in fitness at low populationsize (McCarthy1997, Fischerand Matthies 1998) or at low population density (Gruntfestet al. 1997, Kindvallet al. 1998,Kuussaariet al. 1998,Wells et al. 1998), and has even been erroneouslydefinedas negativedensitydependence(Levitanet al. 1992).Other authorshave demonstrateddecreasesin aspectsof survival or breedingoutput at low numbersor densities, but have not termedthese Allee effects (Carboneet al. 1997,Green 1997,Macedo and Bianchi1997,Storeret al. 1997). We believe that inconsistentuse of the term results from the absence of a single clear definition.In this articlewe aim: (1) to investigatethe originsof the term and to developa much-neededdefinition;(2) to explore the distinctionbetweenthe componentAllee effect, of particular interest to behaviourists,and the demoOIKOS 87:1 (1999) graphicAllee effect, of overridingconcernto conservationists;and (3) to clarify two of the centralareas of confusionwithin the definition-those regardingissues of scale and demographicstochasticity. In order to clarifythe meaningand use of the term Allee effect, we focus attentionon a limitednumberof examplesof mechanismsof this effect. For those unfamiliarwith the rangeof mechanismswhichmay lead to Allee effects,thesehave been reviewedmoreextensively elsewhere (Dennis 1989, Fowler and Baker 1991, Stephens and Sutherlandin press). In brief, these benefits of conspecificpresence may include one or more of: predatordilution or saturation;antipredator vigilance or aggression;cooperativepredation or resourcedefence;socialthermoregulation; collectivemodificationor ameliorationof the environment;increased availabilityof mates;increasedpollinationor fertilisation success;conspecificenhancementof reproduction; and reductionof inbreeding,genetic drift, or loss of integrityby hybridisation. Originsof the term Allee was initially stimulated by an example only loosely linkedto the currentinterpretationof the Allee effect: he showed that goldfish grew faster in water which had previouslycontainedother goldfish,than in water that had not (Allee 1931). Furtherexperiments with a rangeof speciesshowedthat largergroupsize or some degreeof crowdingmay stimulatereproduction, prolong survivalin adverseconditions (throughresistance to desiccationor by social thermoregulation) and enhance protection from toxic reagents (Allee 1931, 1938).Allee saw these phenomenaas 'automaticcooperation',believingthat the beneficialeffectsof numbers of animalspresentin a populationrepresenteda funda185 mental biologicalprinciple(Allee 1938).By 1953 E. P. Odumwas referringto 'Allee'sprinciple'as the concept that "undercrowding(or lack of aggregation)may be limiting" (Odum 1953: 154). Perhaps inevitably, we discovered that similar observationshad been made previouslyby Darwinwho noted that, "in many cases, a large stock of individualsof the same species, relatively to the numberof its enemies,is absolutelynecessary for its preservation"(Darwin 1872:86). Reduction in fitness or populationgrowth at low abundancehas receivedconsiderableattentionin conservationgenetics, under such guises as the '50/500 rule' (Soule and Wilcox 1980), and is also widely debated in fisheries science, where it is usually referredto as depensation (Myers et al. 1995, Liermannand Hilborn 1997). Depensationis principallya populationlevelphenomenon, whichmay or may not arisefrom changesin individual fitness,and thus need not be directlyanalogousto the Allee effect. (a) (c) (b) (d) Flock size Fig. 2. ComponentAllee effects and demographicAllee effects.A mechanismsuchas vigilanceamonga groupmay give rise to a componentAllee effect (shortdashes).Whetherthis results in a demographicAllee effect will depend on the strengthof negativedensity dependenteffects (long dashes), suchas interferenceand depletion.Overallfitness(solidline)is shown for (a) strong,(b) intermediate,and (c) weak negative densitydependence.(d) A sigmoidcomponentAlleeeffectmay lead to demographicAllee effects at intermediatepopulation sizes. effect as: a positive relationshipbetween any component of individualfitnessand eithernumbersor density Definition of conspecifics. In the spirit of Allee's original observations,this the Allee effect is Although reasonablywell known,the definition requiresthat some measurablecomponentof a has of not all of which are concept range meanings, acknowledgedby contemporaryuse. Allee did not the fitnessof an organism(e.g. probabilityof dying or providea definitionbut he clearlyconsidered"certain reproducing)is higher in a large population.Whether aspects of survival values" (Allee et al. 1949: 396) all componentsof mean fitnesscombineto producean rather than total fitness and we thus define the Allee overallincreaseor decreasewith increasingabundance will dependon the relativestrengthof negativedensity dependence.We suggest that it is thereforeimportant (a) to differentiate between component Allee effects (Allee (c) effects manifestedby a componentof fitness)and de- 0 mographic Allee effects (Allee effects which manifest at (b) + (d) + dn \C 0On toincreases kn- *s^ I~wardsk d-n -s n increases towards U U 0 ndt /1/ decli nes dcraes ~k ^/ to extinction ~owards - n decreases I towardsUI Abundance Fig. 1. Negativedensitydependenceand the Allee effect. (a) As populationsgrow there will often be reductionsin the fitnessof individuals,for examplefromincreasingcompetition and depletionof resources,resultingin decreasednatalityand survival.(b) Populationgrowthrate will declinelinearlywith increasingabundance,as illustratedby the logistic equation, giving a single, stable equilibrium(k). (c) For many species however, there are benefitsassociatedwith the presenceof conspecifics.At low numbersor densities,the benefitsfromthe additionof each successiveindividualoutweighthe costs, such that there is a net gain in individualfitness, and fitness is highestat intermediatenumbersor densities.(d) In this case, population growth rate may also be low at low levels of abundance,as shown by the adjustedlogistic equation. If growthbecomesnegativeat low numbers,two equilibriawill result:a lower,unstableequilibrium(C) and an upper,stable equilibrium(U). 186 the level of total fitness).As an illustration,largerbird flocks are (up to a point) more likely to detect predators early, thus reducingtheirmortalityrate (Kenward 1978). There are also likely to be negative effects of increasingnumbers,such as interferenceand depletion of food resources,and a variety of relationshipsbetween these componentsof fitness and flock size are possible (Fig. 2). Although the positive effect of increasingflock size on vigilanceis consistent,only where negativedensity dependenteffects are weak is there a positive relationshipbetweentotal fitness and number at any stage. Thus, componentAllee effectsare seen in all Figs 2a-d, whilstdemographicAllee effectsare seen only in Figs 2c and d. The overallrelationshipbetween fitness and abundancemay be seen as the cumulative effects of all componentAllee effects and all negative densitydependenteffects,or as Allee himselftermedit, all terms of cooperationand disoperation(Odumand Allee 1954). In practice,distinguishingbetweencomponentAllee effectsand demographicAllee effectsmay enableAllee effectsto be describedwith greatercertaintyin the field. The instabilityof the lower equilibrium(see Fig. Id) OIKOS 87:1 (1999) means that natural populations subject to a demographic Allee effect are unlikely to persist in the range of population sizes where that effect is manifest. It has been observed that empirical data on Allee effects are sparse (Dennis 1989, Kuussaari et al. 1998). Establishing whether an observed component Allee effect will lead to a demographic Allee effect is further complicated by the effects of environmental variability on the strength of negative density dependence, and by a potential lag between component and demographic Allee effects. For example, in colonial breeding birds, higher fledging success due to increased colony size could be negated due to greater over-winter mortality of young, perhaps as a result of increased competition for food and hence decreased fat reserves before winter. The component Allee effect of increased fledging success would not be translated into a demographic Allee effect, due to the seasonal nature of negative density dependence. Thus it is interesting to note that whilst theoreticians are principally concerned with demographic Allee effects, empiricists, by the very nature of their work, are usually constrained to the quantification of component Allee effects. In practice, the importance of identifying component Allee effects is usually that their existence indicates the potential for the existence of a demographic Allee effect, which is far less easily demonstrated. a) b) Number, density and issues of scale Widespread confusion over the use of the term Allee effect surrounds the contrast between Allee effects that result from low population sizes and those that result from low population densities. Allee himself did not confront this issue directly but clearly his examples included effects of both number, for example, improved social thermoregulation in larger litters of mice, Mus sp., and of density, for example, increased per capita reproduction among higher densities of flour beetles, Triboliumconfusum (Allee 1938). However, for the majority of mechanisms which lead to Allee effects, the distinction between number and density is complex, depending largely on the spatial resolution at which the system is studied. To the field ecologist, working within a fixed study area, any drop in number will be inseparable from a corresponding reduction in density. Local density may be a more useful measure but still may be difficult to interpret. A useful thought experiment to distinguish between number and density as the basis for a given mechanism is to consider isolated, closed systems, and then compare the consequences of a change in density with those of a concomitant increase in number and area. This approach may be used to distinguish a mechanism such as maintenance of balanced sex ratios that is dependent on numbers of individuals present, from a mechanism C) Fig. 3. Allee effects,populationsize and populationdensity.Determiningwhetheran Allee effectresultsfrom low numbers(n) or low densities(6) of individualsmay be thoughtof in termsof isolatedpatchesor islandsof habitat.The threediagramsshow a) n = 4, 6 = 2, b) n = 16, 6 = 2, and c) n = 4, 6 = 4. Consider a mechanism such as the maintenance of balanced sex ratios. Such a mechanismmay fail as a speciesbecomesrarer,reducingaverageindividualfitnessand causingan Allee effect. In patch (a), thereis a high chancethat both individualsmay be of one sex and that matingmay not take place at all. Highernumbersof individualsin patch (b) reducethe probabilityof such a biasedsex ratio, demonstratingthat increasingnumbersmay alleviate the Allee effect, without an increasein density.Indeed,a highly skewedsex ratio is less likely in patch (b) than in patch (c), despitethe fact that individualsin patch(c) are at the higherdensity.Thus Allee effectsarisingfrom sex ratio skewsresultfrom low numbersof individuals,or small populationsizes. By contrast,considera mechanismsuch as the modificationof soil a phenomenonby whichplantsmay improvelocal conditionsfor growth.Assumingthat an individualplantmay characteristics, have a giveneffecton, say, the pH of a givenvolumeof soil, then plantsin patches(a) and (b) will be equallywell off, and only an increasein density(as in patch (c)) will lead to an increasein individualfitness. OIKOS 87:1 (1999) 187 such as modificationof soil propertiesthat is dependent on densityof individualspresent(Fig. 3). Translationof Allee effects from one temporal or spatialscale to anotheris also dependenton the mechanism involved. Temporalchanges in aggregativebehaviourmay indicatetemporalchangesin the strength of Allee effects.A strikingexampleis that of the mara (Dolichotispatagonum)(Taber and Macdonald 1992). Patchy habitat quality and rapid depletionlead to the highly territorial,monogamousbehaviourof marasfor most of the year. However, despite an abundanceof warrens,puppingis communal,probablyas a resultof the benefitsto pups of increasedvigilanceand improved thermoregulationin communalcreches. Spatialinconsistenciesin Allee effectsmay also occur. Howlermonkeys(Alouattapalliata)on BarroColorado Island, Panama, live in troops of 6-31 individuals (Smith 1977). Individualswithin a group may gain considerablebenefitsfrom the presenceof conspecifics, includingincreasedanti-predatorbehaviour,and cultural transmissionof food-finding and anti-predator information.Troops show considerablerange overlap. Over a period of time, high recruitmentinto a single smallgroupof howlermonkeysmay elevatetheirnumbers considerably.Thus at the local scale of the group, a demographicAlleeeffectmay be seen.At a widerscale however, such an increase in the number of howler monkeysin one troop may cause a markedincreasein the resourcedepletion,loweringthe averagefitness in other groups. fluctuationsmay be usefullyconsideredas a mechanism of the Allee effect. In generaltermsan Allee effect resultingfrom demographic stochasticityis proposed to arise as a consequence of an increasein the variancein the rate of populationchangeor meanfitnessat low numbers.The mechanism for this change in variance is directly analogous to the familiar phenomenon of increased samplingvarianceof the populationmean as sample sizes become small, for example as predictedby the centrallimit theorem.The long-termstochasticdynamics of a populationmay be predictedby transformation of the originalpopulationsize (N) to a new scale (x), such that x = g(N) wherethe transformationg has the propertythat varianceabout the mean fitness is homogenisedas x varies.The most familiarexampleof this 'isotropic'transformationis the geometricmeanpopulation growth rate for population growth of discrete generations in a stochastic environment,i.e. when g(N) = InN (e.g. Lewontinand Cohen 1969).The key featureof this method is that patternsof dynamicsare predictedcorrectlyby x, but not by N. In particular,the mean value of x, which may be termedthe 'dynamic mean' of the population,correctlypredictspopulation persistenceor growth. In the particularcase of the effect of demographic stochasticityon the variance in mean fitness, if the variance resulting from demographicstochasticityis given by c2N, then p(x), the mean value of the change in x at a given value of N, is (Lande 1998): a2g Demographicstochasticity Demographicstochasticityarisesas a consequenceof the discrete rather than continuous nature of biological populationsizes (May 1973);it leads to fluctuationsin percapitagrowthratesthatmay threatenthe persistence of small populations.It has been suggestedthat demographic stochasticityrepresentsa type of Allee effect (Lande 1998) but whetherthis is the case dependson both the definitionof the Allee effectused and the type of demographicstochasticityconsidered.The definition of the Allee effect that we propose above is framedin termsof the effectsof populationsize, or density,on the fitnessof individualsand the consequencesthat thismay or may not have for populationchange.In this respect we contrasttwo categoriesof demographicstochasticity: firstwe considerthe most commonlyinvokedsourceof demographicstochasticity- the randomvariationresultingfromdiscreteindividual(ratherthancontinuous) birthand deathevents(May 1973,Lande 1993);second we considersex ratio fluctuations,also commonlycited as a form of demographicstochasticity(Caughley1994, Lande 1998). Taking these categoriesin isolation, we show that despitethe importantimplicationsof both for population dynamics and persistence,only sex ratio 188 ag a2N p(x) = -FN m2 2 ON ON2 (1) In this case it is assumedthat changeis modelledby a density independent model (AN=rtN) defined by growthparameterr and that demographicstochasticity is the only form of variability.For this model, the appropriatevariance homogenisingtransformationis x = 2/N. Eq. 1 thereforebecomes: (2 (X) = , 4-- 4/N= rx 22 c2 2x 2x (2) The varianceresultingfrom demographicstochasticity reducesthe mean rate of changeof x to below r/2, its maximumvaluein the absenceof demographicstochasticity. The strengthof this reductionis proportionalto the reciprocalof x, i.e. the effect becomesmore important as x becomessmaller,leadingto the proposalthat there is an Allee effect. The importantfeatureof eq. (2), however,is that it is assumedthat demographicstochasticityaffectsonly the varianceabout the mean of N, and not the mean or expectedrateof change(F).This applies,for example,to demographicstochasticity resulting from births and OIKOS 87:1 (1999) deaths.If, for example,the meanprobabilityof deathis d, and the numberssurvivingare predictedby a binomially distributedrandomvariable,then the variancein populationsize is given by Nd(l - d). The varianceis a functionof N, but the probabilityof a randomlychosen individual surviving remains constant at a value of (1 - d). A similar argument could, for example, be developedfor natalityor ratesof recruitment.Although for anypopulationthismechanismwouldleadto increasingprobabilitiesof extinctionwithdecreasingpopulation sizes, expectedindividualfitnesswould not declineconcomitantly. The other form of demographicstochasticitythat is commonlyproposedto lead to reducedratesof change at low densitiesis the effect of populationsize on sex ratios, in particularsex ratio skews at low densities.In thiscasetheeffectof populationsizeon individualfitness is ratherdifferent.Considera species which produces young with, on average,an equal ratio of males(M) to females (F), i.e. the probabilityof producingeither is p(M) =p(F)= 0.5. At very low population sizes (e.g. N = 2), therearethreepossiblepopulationcompositions (allmale,MM;maleandfemale,FM; andall female,FF) whicharisewith probabilitiesp(MM) = 0.25,p(MF) = p(FM) = 0.25, and p(FF) = 0.25. The probabilityof a reproductivepair is thus p(MF) +p(FM) = 0.5 and hence the probability of any individual being in a position to reproduceis also 0.5. As population sizes becomehigh(N-, oo),however,the populationsex ratio will approach1:1,and nearlyeveryindividualwithinthe populationwillbe ableto finda mateof the oppositesex. Hencethe probabilityof an individualbeingin a position to reproduceapproachesunity. The key point to emergeis that the effect of demographicstochasticitythroughbirthsand deathsarisesin a very differentway from the effects of demographic stochasticitythroughpopulationsexratios.In theformer case there is no measurablecomponent of individual fitnessthat is affectedby populationsize or interactions with otherpopulationmembers.The fate of an individual, in termsof its probabilityof dying or reproducing, is unaffectedby the size of the populationwithinwhich it finds itself. In the case of demographicstochasticity throughpopulationsex ratios, on the other hand, the probabilityof an individualbeingableto mateis affected by populationsize, i.e. thereis a measurablecomponent of individualfitnessthat can be relatedto the size of the populationand interactionsbetweenorganisms.Thefate of the populationas a whole is affectedby its size when demographicstochasticitythrough births and deaths occurs.This, however,is not a consequenceof changing fates of the individualswithinthe populationand hence cannot be consideredas an exampleof the Allee effect. A similarargumentcan be used to categorizeother phenomenaarisingfrom low populationdensityor size. Inbreedingdepression,for example,is commonlyproposedto leadto reducedfitnessat low densities.InbreedOIKOS 87:1 (1999) ing could be consideredto generatean Allee effect since the degreeof inbreedingdepressionto whichan individual is subjectdependson the size of the populationinto which it is born. Oneof the importantconclusionswe derivefromthese distinctionsbetweencomponentand demographicAllee effects as well as between the forms of demographic stochasticityis that Allee effectsdo not inevitablylead to impactson net populationgrowth, such as positive densitydependenceandunstablelowerequilibria;neither do the existenceof these implyunderlyingAllee effects. An Alleeeffectat the levelof the populationimpliesthat positive densitydependenceresultsfrom the effects of densityon the fatesof, andinteractionsbetween,individuals within the population. In summary,following our definitionof the Allee effect,whichis closelybasedon Allee'soriginalwork,it is reasonableto includestochasticsex ratio fluctuations as a mechanismleadingto Allee effectsbut misleading to group stochasticbirth and death processestogether with Allee effects. 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