The University of Chicago Seed Dispersal by Animals: Contrasts with Pollen Dispersal, Problems of Terminology, and Constraints on Coevolution Author(s): Nathaniel T. Wheelwright and Gordon H. Orians Source: The American Naturalist, Vol. 119, No. 3 (Mar., 1982), pp. 402-413 Published by: The University of Chicago Press for The American Society of Naturalists Stable URL: http://www.jstor.org/stable/2460937 . Accessed: 24/12/2013 11:41 Your use of the JSTOR archive indicates your acceptance of the Terms & Conditions of Use, available at . http://www.jstor.org/page/info/about/policies/terms.jsp . JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact [email protected]. . The University of Chicago Press, The American Society of Naturalists, The University of Chicago are collaborating with JSTOR to digitize, preserve and extend access to The American Naturalist. http://www.jstor.org This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions March 1982 The AmericanNaturalist Vol. 119, No. 3 SEED DISPERSAL BY ANIMALS: CONTRASTS WITH POLLEN DISPERSAL, PROBLEMS OF TERMINOLOGY, AND CONSTRAINTS ON COEVOLUTION NATHANIEL T. WHEELWRIGHT AND GORDON H. ORIANS Departmentof Zoology, Universityof Washington,Seattle, Washington98195 SubmittedFebruary27, 1981; Accepted September28, 1981 Recent thinkingabout seed dispersal and the coevolutionof fruiting plants and frugivoreshas been stronglyinfluencedby ideas developed throughthe studyof pollen dispersal by animals. Analogies are commonlydrawn between the two systems (Howe 1977; Van der Pijl 1972; Howe and Primack 1975; Howe and Vande Kerckhove 1979; Howe 1979; Howe and De Steven 1979; Howe 1980). Both systemsrepresentcoevolved relationshipsof mutualbenefitto plants and animalsthatinvolvethe disseminationof pollen or seeds and the provisionby the plant of some incentivesuch as nectar or fruit.The evolutionof highdegrees of mutualdependence and morphologicaland behavioral specialization,evident in some pollinationsystems,is assumed also to be likelyin certain seed dispersal systems (Howe and Primack 1975; McKey 1975; Howe 1977; Howe and Estabrook 1977). A rich array of evocative metaphorscurrentlyused in studies of interactions("loyalty," "theft," "reliability," "faithfulness," plant-frugivore "reward," and so on; see McKey 1975 and Howe and Estabrook 1977) reflects conceptual biases apparentlyderived in part fromimplicitand explicitanalogies withpollen dispersal. Althoughsuch termsare sometimesuseful,theymay cloud interactions. the true natureof fruit-frugivore Pollen and seed dispersal are fundamentallydissimilar,particularlyin most characteristicslikelyto influencechoice of diet and foragingitinerariesby animal vectors,and patternsof productionof pollen and fruitby plants. The purpose of this paper is threefold:(1) to outline clearly the relevant differencesbetween pollen and seen dispersal,(2) to indicatesome of the problemsof usingterminology borrowedfromstudiesof pollen dispersalto describe seed dispersalsystems, and (3) to consider the factorsthat may explain the virtualabsence of obligate mutualismsin seed dispersal systems(Howe and Vande Kerckhove 1979). Because of our greaterfamiliaritywith avian frugivoresand their importancein theoreticaland empiricalstudies of seed dispersal, most of our referencesdeal principallywithbirds. Futureworkon seed dispersalby mammals,ants, reptiles, and fishmay offernew insights. Am. Nat. 1982. Vol. 119, pp. 402-413. All rightsreserved. ? 1982 by The Universityof Chicago. 0003-0147/82/1903-0016$02.00. 402 This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions COEVOLUTION THE THEORY OF FRUITING PLANTS AND FRUGIVORES OF FRUIT-FRUGIVORE 403 COEVOLUTION Snow (1971) firstconsidered the consequences of evolutionaryinteractions thatdispersetheirseeds and recognized plantsand the frugivores betweenfruiting theunique attributesoffruitas a food resource.Relativeto other"prey," fruithas evolved to be generallyaccessible, conspicuous, and easily digestiblein orderto attract seed dispersers (Snow 1971). Following Snow's contribution,McKey coevolutionto explain the varietyof (1975) proposed a model of plant-frugivore strategiesplantsuse to dispersetheirseeds in whichhe introducedthe concept of dispersalquality.At one extreme,some plantsproduce manysmall, nutritionally poor fruitsthatattracta wide varietyof "poor quality" dispersers.Alternatively, superiorfruitswhose seeds othersproducea smallernumberoflarge,nutritionally are dispersedby a limitednumberof species delivering"high dispersalquality." Qualityrefersto seed size carriedand the probabilitythata seed removedfroma plantis deposited in viable conditionin a site suitableforgerminationand establishment(McKey 1975). A numberof recent studies, both theoretical(Morton 1973; Howe and Estabrook 1977; Howe 1979; Thompson and Willson 1979; Fleming 1979) and empirical(Smith 1975; Howe 1977; McDiarmid et al. 1977; Thompson and Willson 1978; Howe and De Steven 1979; Howe and Vande Kerckhove 1979; Howe 1980; Howe 1981; Snow 1981) have refinedhypotheses, evaluated some predictions,and providedobservationson fruitremovalrates and trees. behavior of frugivoresat fruiting Centralto currenttheoryis the propositionthatfrugivoresdifferin behavioral and ecological traitsthataffecttheirsuitabilitiesas seed dispersers.If so, under certaincircumstances(e.g., predictableecological requirementsforseeds) natural selectionis expected to lead to the mutualinterdependenceand tightassociation of individual plant species with "one particularlyeffectivedisperser" (Howe 1977),or a small numberof obligatefruigivores(McKey 1975; Howe and Primack 1975; Howe and Estabrook 1977). However, empirical studies have generally failedto discover eitherhighlycoevolved frugivoresor plantsadapted to exclude all but a single disperser, as in some (though much fewer than generallyapcounterpartsto preciated) pollen dispersal systems.The lack of plant-frugivore specialized pollinationsystems,such as orchids (Dressler 1968; Dodson 1975) or Dalechampia (Armbrusterand Webster 1979) and euglossine bees, or yucca species and the mothTegeticula (Powell and Mackie 1966), is striking(see also Galil 1977; Sazima and Sazima 1978; Thien 1969). The majorityof studiesof birds, at least, have documentedinstead a tremendousdiversityof frugivoresat fruiting trees (Eisenmann 1961; Land 1963; Willis 1966; Diamond and Terborgh 1967; Jenkins1969; Leck 1969; Haverschmidt1971; Cruz 1974; Wheelwrightet al., in prep.). Not onlydo manybirdspecies feed on thefruitofa singleplantspecies, but also they may represent up to 13 families (McDiarmid et al. 1977). Even the "specialized," high reward fruitsof some Lauraceae (McKey 1975) may have theirseeds dispersedby morethan 17 species of birdsfromat least eightfamilies (Wheelwright,in prep.). Morphologicallyas well as taxonomically,birdsfeeding et on thefruitsofthe same treemaybe quite different (Ricklefs1977; Wheelwright al., in prep.). This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions THE AMERICAN NATURALIST 404 The discoveryofassemblages of manyspecies ofdiversefrugivores, ratherthan limitedassociations, spawned a deprecatingterminologyto referto species presumed to be poor dispersers: "opportunists,exploiters" (McKey 1975), "fruit thieves" (Howe and Estabrook 1977), and "parasites" (Janzen 1977). Such metaphorsreflectthe expectations of the theorymore than they do the actual effectsof the frugivores;data do not yetexistto evaluate accuratelythe effectiveness of dispersalby different species. Despite thefactthatmanystudiespurportto deal with seed dispersal, most reportonly observationson who removes fruit, how regulartheyare as visitors,and, in some cases, whetheror not theydestroy seeds. The above terminologyobscures the fact thatfrugivoresrepresenta continuumin termsof the numberof seeds each species deposits in suitablesites and the probabilitythat it gives an individualseed favorabletreatment. SEED DISPERSAL VERSUS POLLEN DISPERSAL Pollen dispersaldiffersfromseed dispersalin several fundamentalrespectsthat preventcomparableprecisionin seed dispersal (table 1). First,pollen has a very specific"target," the stigmaof a nonspecificflower.These flowersare usually easily recognizedbecause of theirdistinctivecolors, scents, and morphology.In contrast,a seed's "objective," a site suitableforgermination, establishment,and ultimatelyreproduction,is more difficult to characterizein space and time. Appropriatesites for seeds have few distinguishing featuresperceptibleby frugivores, althoughfrugivoresmaypreferentially frequentcertainhabitattypes. On a gross scale, some habitat types (flood plains, riverbanks)may be predictable (Howe and Estabrook 1977), but withinthem sites for seeds are not. Moisture, sunlight,soil nutrients,seed and seedlingpredators,herbivores,fungalassociates, allelopaths,and othersubtle factorsdeterminewhethera site is a good one fora seed. Moreover, conditionsmay easily change and characteristicsof a site at the time a seed is deposited may be poor indicatorsof futurequality. Second, pollen dispersaldiffersfromseed dispersalin the temporalavailability of suitable sites. Antherdehiscence and pollen dispersal are coordinated with stigmareceptivityin synchronouslyfloweringpopulations,but opportunitiesfor successfulseedlingestablishment(e.g., lightgap formation)may occur randomly in time and space (Poore 1967; Knight 1975; Hartshorn1978). Third,floweringplantsbenefitfromhabitatspecificityand sequentialvisitation of nonspecificplants by theirpollen vectors because visits to flowersof other species may resultin pollen transferto inappropriate"targets" and consequent waste of pollen. A similaradvantage has been suggestedforfruiting plants when host-specificfrugivorescarryseeds to the habitatsoccupied by nonspecificplants (Howe and Primack1975; Howe and Estabrook 1977). Yet, ifspecies-specificseed and seedling predationis greaternear nonspecifictrees (Janzen 1970; Connell 1971), selection should not favorspecialized diets and movementsby dispersers betweentreesof the same species. Moreover,the presence of an adultnonspecific plantis not necessarilyevidence of an appropriatesite fora seed, particularlyin thecase of shade-intolerant plants,whichcomprisethemajorityof canopy species in some tropicalforests(Hartshorn 1978) where up to 90% of plant species are animal dispersed (Frankie et al. 1974). Once a tree reaches the canopy, its shade This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions COEVOLUTION OF FRUITING PLANTS AND FRUGIVORES 405 TABLE 1 GENERALDIFFERENCESBETWEENPOLLEN DISPERSALAND SEED DISPERSAL PollenDispersal Suitable site for dispersal .... Characteristics of siteas predictorsof suitability....... stigmaof conspecificflower Seed Dispersal site appropriateforgermination and establishment distinctive: color,shape,etc.; unpredictable: manysubtle oftenapparentat a distance factorsinvolved;present characteristics oftenpoorindicatorsof future Temporalpattern of suitable quality sites ..................... synchronous withpollendisunpredictable: oftenindepersal pendentof habitattypeor phenology of nonspecific plants Advantage forplantofdietand habitatspecificity by animal vector ................... high:most pollen lost ifvisitsto low: presence of adult conother species of plants interspecificplantoftenan unsuitvene between visits to conable site because of densityspecifics dependentseed predationor different habitatrequirements Abilityof plantto directanimal of seed and tree vectors to suitable site .... high:incentives(nectar,pollen, low: no incentiveforfrugivore etc.) providedat suitable site to deposit seed in favorable site; seed representsheavy and space-consumingballast thatis profitably discarded as quickly as possible. has changed the favorablemicrohabitatthat allowed its own establishmentas a seed and seedling. Perhaps the most fundamentaldistinctionbetween pollen dispersal and seed dispersal systems is the abilityof the plant to manipulatethe behavior of the animal vector. Floweringplants can controlpollinators'movementsto a greater extentby providingnutritional (Baker and Baker 1975) and reproductive(Dodson 1975) incentivesat the appropriatesite (flower)forpollen transfer.There is, in effect,"paymentupon delivery." There is no similarincentiveforseed dispersers to drop seeds in appropriateplaces. Fruitingplants sufferthe costs of "advance payment":Once frugivores have strippedseeds oftheirnutritiousfruit,thereis no furtheradvantage in carryingthe "ballast" (Snow 1971) which, unlike pollen, or defecationof may be heavy and space consuming.Hence, rapid regurgitation the seed benefitsthe disperser,irrespectiveof its advantageto the plant.For both pollinatorsand frugivores,the delayed returnbenefitsof "altruistic" pollen or seed dispersal(such as futureincreases in local floweror fruitavailability)maybe discounted (see also Howe and Estabrook 1977). Given these limitations,to whatdegreemightplantsbe able to manipulatetheir potentialseed dispersers?It has been suggestedthatmorphological,chemical,and phonologicalcharacteristicsof plants and theirfruitsmay induce frugivoresto leave fruiting trees afterconsumingfew fruits.Amongthe conceivable incentives are limited levels of fruitproduction (Howe 1977), mild toxicity,nutritional This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions 406 THE AMERICAN NATURALIST inadequacy of fruits,bulkyor slowlydigestiblefruits,and structuralmodifications of the plantto increase the riskof predation.Whetherthese are "adaptations" or consequences of otherlifehistorydemands (defense againstfungal,bacterial,or insect fruitand seed parasites; limitationsof energyor nutrients;photosynthetic considerations,etc.) remainsuncertainat this point. In any event, plants cannot directthe dispersal of seeds to a particularlocation with a degree of exactness comparable to pollen dispersal,thoughpossibly theycould favoranimal vectors withparticularbehaviors(Docters van Leeuwen in McKey 1975), habitatpreferences, or probabilisticpatternsof seed dispersal (Smith 1975; Howe 1977; Howe and Primack 1975). of directingseed vecand the difficulty Thus, environmentalunpredictability constrain seed if suitable sites were dispersal systems "knowable," tors, even fromachievingthe precisionand specializationof some pollen dispersalsystems. "SPECIALIZATION" IN PLANT-FRUGIVORE INTERACTIONS Justas comparisonswithpollen dispersal have led to unrealisticexpectations about coevolved mutualismsin seed dispersalsystems,impreciseand inconsistent has affectedtheoreticaldevelopmentsand interpretation of empirical terminology observations.For example, the term"specialist" is used frequentlywithrespect to fruit-frugivore interactions.Basically thetermrefersto theuse ofonlya portion ofthetotalarrayof available resources. No organismis a puregeneralist,usingall potentialresources in proportionto theiravailability,but, because species differ in the extentto whichthey are selective in resource use, the term"specialist," even thoughit is inevitablyimprecise,is useful forcomparingspecies. A firstsource of confusionarose because the degreeto whicha frugivoreshould be considereda "specialist" has been assessed by different criteria:beingtotally or mostly frugivorous(Snow 1971); feeding only fruitto its nestlings("total frugivory";Morton1973); relyingsolely on fruitas its source of proteinand lipids (McKey 1975); and beingan animalthatis "totallydependenton fruitforfood for at least part of its life and which invariablyvoids or regurgitatesseeds in viable condition" (Howe and Estabrook 1977,p. 818). Snow (1981) definesa specialistin termsof the qualityand size of the fruitsit eats. The bearded bellbird(Procnias averano) is oftencited as the archetypal"specialist" (McKey 1975), despite the fact that it actually feeds on at least 40-50 species of fruit(Snow 1970) and probablyinsects and lizards as well (based on personal observationsof its congenorP. tricarunculataand othertropicalfrugivores).All of the above notions have value, buttheuse of a singletermto referto such disparatecharacteristicsis certainto fostercontinuedconfusion.It would be preferableto use more precise termsto referto particularpatternsof resourceuse, such as "principallyfrugivorous." Moreover, the term "specialist" is totallyinappropriatewhen applied to characteristicsunrelatedto resource use, such as dispersal quality. A second problem arises with respect to the concept of a "specialized dispersal system." Specialization in plant-animalmutualismshas two components that must be distinguished.A fruitingplant, for example, may specialize with regardto its seed dispersers:Its seeds maybe principallydispersedby onlyone or This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions COEVOLUTION OF FRUITING PLANTS AND FRUGIVORES 407 a few of the arrayof potentialfrugivores.A fruit-eating animal,in turn,may be a specialist by restricting the major part of its diet to a small subset of the fruits available. In principle,therefore,a plant could specialize on a few generalist dispersers,just as a frugivorecould specialize on a plant dispersed by many species. Moreover, there is no a prior reason to expect a strongcorrelation betweenthe degree of specializationand the importanceof a plantto a frugivore and vice versa. A frugivoremay be veryimportantto a plantin a situationwhere neithertheplantnorthefrugivoreis a specialist(e.g., thetreeCasearia corymbosa [=C. nitida] and the masked tityra,Tityrasemifasciata; Howe and Primack1975; Howe 1977; also Noble 1975). Pollen and seed dispersal systemsdifferin the extentto which plants benefit fromspecialization, eitherin termsof being dispersed by a limitednumberof potential dispersers or attractingdiet-specificanimal vectors. In the case of floweringplants,entrainedpollinatorsreduce the incidence of hybridizationand wasted investmentin lost pollen and inviable seeds, and increase the amountof pollendeliveredto suitablesites. Pollinationby species-specificvectorsallows the persistenceand reproductionof plants when populationdensitiesare low (Baker and Hurd 1968; Janzen1971). Because of the relativeprecisionof pollen transfer, natural selection can favor the evolution of complex flowersthat exclude or discourageorganismsunlikelyto transferpollen to nonspecificstigmaswithlittle adverse effecton pollinationsuccess. Not surprisingly,there are examples of flowersthat attractonly one or a few pollinatorswith narrowdiets ("specialize on specialists"; see referencesabove). The potentialvalues to plants of having only a few kinds of seed dispersers depend on both treatmentof seeds and the way they are deposited into the environment.If onlya singlefrugivorespecies regularlyvisitsa plant,mostof the plant's seeds receive similartreatment.Eitherseeds willbe regurgitated or, ifthey pass throughthe digestivetract,theywillencountersimilarchemicaland physical to withconditions(McKey 1975). Therefore,an optimalseed coat just sufficient butnotso tough standtheabrasionreceivedby the seed in thegutofthefrugivore, as to inhibitsubsequentgerminationor cause waste of resources in the construction of unnecessarilystrongcoats, can evolve. Birds thatrelyon fruitsforall or nearly all of their nutritionalneeds are believed to have soft-linedgizzards (McKey 1975), and many of them regurgitateseeds. However, it is likely that soft-linedgizzards evolved to avoid digestionof toxic, thin-coatedseeds rather is advantageous than to provide gentletreatmentto the seeds, and regurgitation because it quickly reduces the indigestibleballast carried by the frugivore. In general, the smallerthe numberof species of frugivoresthat visit a plant species, the fewerthe habitattypes in whichits seeds are likelyto be deposited. However, withinthose habitats,suitable sites forseed germinationand seedling establishmentmay arise unpredictably.Because of seed dormancyor seedling longevity,sites may be occupied long beforetheyarise (Howe 1980). Therefore, unless there are strongtemporal correlationsbetween the sites visited by a particulardisperser and the present or futureavailabilityof suitable sites, the potentialadvantage of havingonly a restrictedset of seed dispersersmay not be realized (Howe 1977). This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions 408 THE AMERICAN NATURALIST Set against these possible advantages of restrictingthe array of frugivores regularlyvisitinga plant,thereare a numberof advantageslikelyto be associated withattractingmanykindsof dispersers.First,thelargerthe numberof species of frugivores,the greaterthe numberof dispersingindividualsand the largerthe numberof fruitsthatcan be removed fromthe tree per day (Snow 1971). Since fruitsmay oftenrot on trees or fallto the groundwithouthavingbeen consumed (personal observation; Howe 1981), there are often situationsin nature when having more visitorswould probablybe beneficial. Second, a fruitcapable of being dispersed by a varietyof frugivoresis not limitedto the habitat or general geographicalrange of any single disperser (a restrictionin some pollinationsystems;Baker and Hurd 1968) and can expand its distributionto colonize new sites (Hamilton and May 1977). Third,plantsthatrelyon manyspecies to dispersetheirseeds may have a lower probabilityof extinctionif a single disperserbecomes extinctor becomes very rare (Howe 1977; Howe and Vande Kerckhove 1979; Temple 1977; Gilbert1980). However, the evolutionof such "bet-hedging"strategieshas yetto be supported by geneticmodels of naturalselection at the level of the individual(Slatkin and MaynardSmith1979). High ratesof populationturnover,probablyeven greaterin the tropicswhere manyspecies have low populationdensitiesand poor dispersal abilities(Willis 1974), may mean thatfruiting plantsare rarelyin association long enough with specificfrugivoresto evolve tightobligate mutualismseven if they were favored over the shortterm. Fourth,even thoughthe mean probabilityof seed survivalmightbe lower in seed distributionsproduced by dispersersof many species than in distributions produced by a singlehighqualitydisperser,naturalselectioncould favorattractingmanydispersersratherthana singleone (fig.1). Whetheror notthe right-hand tail of the seed distribution curve generatedby manydisperserslies further to the rightthanthatgeneratedby a singledisperserdepends, of course, on the relative availabilitiesof dispersersand on theirbehavior. But since a tree may produce hundredsto millionsof seeds duringits lifetime,each with an extremelylow probabilityof survival (given the fact that each plant leaves, on average, one in an equilibrialforest),countingon a singledispersermaybe analogous offspring to Williams' (1975) assessmentof asexual reproduction:the multiplepurchase of the same lotteryticket. Unfortunately,testingthis hypothesisdirectlyis extremelydifficult.Of the many seeds produced, findingthe survivingseedlings is difficult.Knowing their parents and their dispersers seems almost hopeless. Althoughthe probability of survival of any one seed is extremelylow, whetheror not the possibilityof improvingthatprobabilityis favoredby naturalselectiondepends on the value of alternativeuses of energyby the plant. For adult plants that have reached the canopy or theirnormalfull size, alternativeuses of energyor nutrientsshould normallyhave verylow marginalvalues, favoringheavy investmentsin reproduction even when the marginalvalue of incrementsto reproductiveinvestmentsare as low as theynormallymustbe formostplants. The real meaningof "waste" in seed dispersal (Howe 1980) is thereforeunclear. Viewing the problemfromthe point of view of frugivoresalso suggeststhat under most circumstanceseating a varietyof fruits,plus animal foods as well, This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions OF FRUITING PLANTS AND FRUGIVORES COEVOLUTION ( w 409 Dispersal by many species In addition to 'sigh quality disperser (I) 0~ (n 0 w w | \ispersa/ by "high quality" a/one >(! /disperser LAL 0/ W~~~~~~~~~~~~~~~~~~~~ D/ zTALL LOW DL(PERLER /PECIE5) S SUITABILITY OF SITES IN WHICH SEEDS X// GH OUAL/TY A HIGH ARE DEPOSITED FIG. 1. Suitabilityof seed dispersalby a wide assemblage of dispersers(solid line), versus by a single"high quality" disperser(dashed line). If only those seeds deposited in the best sites (to the rightof pointA) are likelyto survive,naturalselectionwillfavortheattractionof a diversedisperserassemblage in spiteof itslowermean dispersalquality(cf. Williams1975). should normallybe favored. Very few plants fruitthroughoutthe year, and few are commonin morethana limitedpartof theirrange. Moreover,mostfrugivores (with the exception of ants) are moderate-sized,relativelylong-livedorganisms thatcannot package theirannual cycle withina singlefruiting season theway that a numberof large,principallyfrugivorous manypollinatorsdo. Not surprisingly, birds undergo markedseasonal movementsduringthe year in response to local variations in fruitabundance (personal observation). Few dispersers are constantlyreliable in the sense of McKey (1975) and Howe and Estabrook (1977). Also, frugivoresthatmay providehighqualitydispersal at one timeof the year may not do so at other times. The obligatelyfrugivorousoilbird (Steatornis caripensis) roosts and nests in caves where most of the seeds it ingests are deposited (Snow 1962); bellbirds and manakins typicallydrop seeds beneath displayperches duringthebreedingseason (personal observation).Althoughthey probablygive all seeds gentletreatment, theyare usuallylow qualitydispersersat such times in termsof the sites where they deposit seeds. CONSTRAINTS ON COEVOLUTION We have argued that finelytuned mutualisticrelationshipsin seed dispersal systemsshould be rare forthe followingreasons: (1) the inabilityof the plant to provide incentivesfor precision in seed dispersal; (2) the relativelysmall dif- This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions 410 THE AMERICAN NATURALIST ferencesamong frugivoresin seed dispersal quality; (3) the unpredictability and of recognitionof suitabletargetsforseeds; (4) the potentialadvantages difficulty of having a broad assemblage of dispersers; and (5) the nature of life cycles of frugivores.There may also be evolutionaryconstraintson developinga restricted assemblage of seed dispersers(cf. Janzen 1977). For example, in Costa Rica's lower montane wet forest,both mountainrobins (Turdus plebejus) and whitethroatedrobins (T. assimilis), as well as manyotherspecies, feed on lauraceous fruits.The habitat preferencesand foragingpatternsof the two species differ markedly(personal observation). They may also differin some measure of disto imaginewhat adaptationsa plant could use to persal quality,yet it is difficult exclude the poorerdisperserwithoutbarringits morphologicallysimilarcongener as well. Classes of disperserscould be favoredby alteringfruitsize (McKey 1975; Howe and Estabrook 1977), heightof presentation(L. Best, in prep.), firmnessof attachment,color, nutritionand manyotherfeatures.These traits,however,are likely simplyto reduce the diversityof visitors(possibly excluding some good dispersers), not to limitit to a single species. Equally importantmay be the influenceof spatial heterogeneityand gene flow (Howe and Vande Kerckhove 1979). Geographicalregionsdifferin theproportion of habitattypes and the pool of available dispersers.Even over relativelyshort distances totally differentfrugivoresmay feed on the fruitsof the same tree species. Thus, ifthereis gene flowbetweenpopulationsof a tree species, it may not evolve adaptationsto exclude poor dispersersin one area because the same tree in anotherplace is visitedby a different groupof brids. Gene flowprobably constrainscoevolutionof one-to-onemutualismsin pollinationsystemsas well. Under what conditions would one expect to find highlycoevolved mutualisms between fruitingplants and frugivores?Two accounts document obligate mutualisms(fromthe plant's perspective;Rick and Bowman 1961; Temple 1977). Interestingly, bothofthese associations occur on islands,whereenvironments are relativelyuniform,faunasare impoverished,and populationsare isolatedfromthe homogenizinginfluenceof gene flow. SUMMARY Theoretical and empiricalresearch on frugivoryand seed dispersal has been influencedby concepts derived from the study of pollination. In particular, explicitand implicitanalogies between seed dispersal and pollen dispersal have led to the expectation, under certain conditions, of the evolution of obligate, species-specificrelationshipsbetweenfruiting plantsand theanimalsthatdisperse theirseeds. The two systemsdifferin importantrespects,however. Plantsbenefit by directingpollen dispersersto a definite,recognizable "target," a nonspecific flower,and theycan provideincentivesat flowerswhichserve to attractpotential pollinators.In effect,thereis "paymentupon delivery" of the pollen. In contrast, for seeds the target(an appropriatesite for germinationand establishment)is seldom readilydiscernible,and dispersalbeneatha nonspecificplantmay actually be undesirable. Another importantdifferenceis that frugivoresare "paid in advance." Because of these differencesand others,the outcomes of coevolution This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions COEVOLUTION OF FRUITING PLANTS AND FRUGIVORES 411 thanthose of flowerplantsand frugivoresare expected to be different of fruiting ing plants and flower visitors. There are thereforeproblems with drawing derivedfromstudiesof analogies betweenthe two systemsand usingterminology pollinationto design and interpretstudies of seed dispersal. ACKNOWLEDGMENTS We appreciatethe interestand insightscontributedby the Ecology and EvolutionaryBiology groupat the Universityof Washingtonduringvarious discussions of these ideas. L. Best, M. Gardner,W. Haber, H. Howe, S. Koptur, E. Leigh, offeredhelpfulcommentson an earlierdraft.A suggestionby and A. Worthington M. Westoby promptedthe use of fig. 1. The firstauthor received generous financialsupportfromthe Organizationfor Tropical Studies and Sigma Xi for research in Costa Rica. LITERATURE CITED Armbruster,W. S., and G. L. Webster. 1979. Pollinationof two species of Dalechampia (Euphorbiaceae) in Mexico by euglossine bees. Biotropica 11:278-283. coevolution. Baker, H. G., and I. Baker. 1975. Studies of nectar constitutionand pollinator-plant Pages 100-140 in L. E. Gilbertand P. H. Raven, eds. Coevolution of animals and plants. Universityof Texas Press, Austin. Baker, H. G., and P. D. Hurd. 1968. Intrafloralecology. Annu. Rev. Entomol. 13:385-414. Connell,J. H. 1971. On the role ofnaturalenemies in preventingcompetitiveexclusion in some marine animals and in rain foresttrees. Pages 298-312 in P. J. den Boer and G. R. Gradwell, eds. Proceedingsof the Advanced Study Instituteon dynamicsof numbersin populations,Oosterbeek, 1970. Centre for AgriculturalPublishingand Documentation,Wageningen. Cruz, A. 1974. Feeding assemblages of Jamaicanbirds. Condor 76:103-107. and feedingassemblages Diamond, J. M., and J. W. Terborgh.1967. Observationson birddistribution along the Rio Callaria, Departmentof Loreto, Peru. Wilson Bull. 79:273-282. Dodson, C. H. 1975. Coevolutionof orchidsand bees. Pages 91-99 in L. E. Gilbertand P. H. Raven, eds. Coevolution of animals and plants. Universityof Texas Press, Austin. Dresser, R. L. 1968. Observationson orchids and Euglossine bees in Panama and Costa Rica. Rev. Biol. Trop. 15:143-183. Eisenmann, E. 1961. Favorite foods of Neotropical birds: flyingtermitesand Cecropia catkins. Auk 78:636-638. Fleming,T. H. 1979. Do tropicalfrugivorescompete for food? Am. Zool. 19:1157-1172. Frankie, G. W., H. G. Baker, and P. A. Opler. 1974. Comparative phenologicalstudies of trees in tropical wet and dry forestsin the lowlands of Costa Rica. J. Ecol. 62:881-919. Galil, J. 1977. Fig biology. Endeavour 1:52-56. Gilbert,L. E. 1980. Food web organizationand theconservationof neotropicaldiversity.Pages 11-34 in M. E. Soul6 and B. A. Wilcox, eds. Conservationbiology. Sinauer, Sunderland,Mass. Hamilton,W. D., and R. M. May. 1977. Dispersal in stable habitats. Nature 269:578-581. Hartshorn,G. S. 1978. Tree fallsand tropicalforestdynamics.Pages 617-638 in P. H. Tomlinsonand M. N. Zimmerman,eds. Tropical trees as living systems. Cambridge UniversityPress, Cambridge. Haverschmidt,F. 1971. Large numbers of birds exploitinga fruittree in Surinam. Wilson Bull. 83:104-105. Howe, H. F. 1977. Bird activityand seed dispersalof a tropicalwet foresttree. Ecology 58:539-550. 1979. Fear and frugivory.Am. Nat. 114:925-931. 1980. Monkey dispersal and waste of a neotropicalfruit.Ecology 61:944-959. This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions 412 THE AMERICAN NATURALIST . 1981. Fruitproductionand animal activityin two tropicaltrees.In E. Leigh, Jr.,A. S. Rand, and D. M. Windsor,eds. The ecology of a tropicalforest:seasonal rhythmsand long-term changes. SmithsonianInstitution,Washington,D.C. Howe, H. F., and D. DeSteven. 1979. Fruitproduction,migrantbirdvisitation,and seed dispersalof Guarea glabra in Panama. Oecologia 39:185-196. Howe, H. F., and G. F. Estabrook. 1977. On intraspecific competitionforavian dispersersin tropical trees. Am. Nat. 111:817-832. Howe, H. F., and R. B. Primack. 1975. Differential seed dispersalby birdsof the treeCasearia nitida (Flacourtiaceae). Biotropica 7:278-283. Howe, H. F., and G. A. Vande Kerckhove. 1979. Fecundityand seed dispersal of a tropical tree. Ecology 60:180-189. Janzen,D. H. 1970. Herbivoresand the numberof tree species in tropicalforests.Am. Nat. 104:501528. 1971. Euglossine bees as long-distancepollinatorsof tropical plants. Science 171:203-205. 1977. Promisingdirectionsof studyin tropicalanimal-plantinteractions.Ann. Mo. Bot. Gard. 64:706-736. Jenkins,R. 1969. Ecology of threespecies of Saltatorswithspecial referenceto theirfrugivorousdiet. Unpubl. Ph.D. diss. Harvard University. Knight,D. H. 1975. An analysis of late secondary succession in species-richtropicalforest.Pages 53-59 in F. B. Golley and E. Medina, eds. Tropical ecological systems.Springer-Verlag, New York. Land, H. C. 1963. A tropicalfeedingtree. Wilson Bull. 75:199-200. Leck, C. F. 1969. Observations of birds exploitinga Central American fruittree. Wilson Bull. 81:264-269. McDiarmid,R. W., R. E. Ricklefs,and M. S. Foster. 1977. Dispersal ofStemmadeniadonnell-smithii (Apocynaceae) by birds. Biotropica 9:9-25. McKey, D. 1975.The ecologyof coevolved seed dispersalsystems.Pages 155-191in L. E. Gilbertand P. H. Raven, eds. Coevolution of animals and plants. Universityof Texas Press, Austin. in tropicalbirds. Morton,E. S. 1973. On theevolutionaryadvantagesand disadvantagesof fruit-eating Am. Nat. 107:8-22. of the Noble, J. C. 1975. The effectsof emus (Dromaius novaehollandiae Latham) on the distribution nitrebush (Nitraria billardieriDC.). J. Ecol. 63:979-984. Poore, M. E. D. 1967. The concept of the association in tropicalrain forest.J. Ecol. 55:460-470. of moths and Yucca whipplei Powell, J. A., and R. A. Mackie. 1966. Biological interrelationships (Lepidoptera: Gelechiidae, Blastobasidae, Prodoxidae). Univ. Calif. Publ. Entomol.42:1-46. Rick, C. M., and R. I. Bowman. 1961. Galapagos tomatoes and tortoises. Evolution 15:407-447. functionanalysis of assemblagesof fruit-eating Ricklefs,R. E. 1977. A discriminant birds in Central America. Condor 79:228-231. Sazima, M., and I. Sazima. 1978. Bat pollinationof the passion flower,Passiflora mucronata, in SoutheasternBrazil. Biotropica 10:100-109. Slatkin,M., and J. Maynard Smith. 1979. Models of coevolution. Q. Rev. Biol. 54:233-263. Smith,A. J. 1975. Invasion and ecesis of bird-disseminated woody plantsin a temperateforestsere. Ecology 56:19-34. Snow, B. K. 1970. A fieldstudy of the bearded bellbirdin Trinidad. Ibis 112:299-329. Snow, D. W. 1962. The natural historyof the oilbird (Steatornis caripensis) in Trinidad, W.I. II. Population, breedingecology and food. Zoologica 47:199-221. 1971. Evolutionaryaspects of fruit-eating by birds. Ibis 113:194-202. 1981. Tropical frugivorousbirds and theirfood plants: a world survey. Biotropica 13:1-14. Temple, S. 1977. Plant-animalmutualism:coevolution with dodo leads to near extinctionof plant. Science 197:885-886. Thien, L. B. 1969. Mosquito pollinationofHabenaria obtusa (Orchidaceae). Am. J. Bot. 56:232-237. Thompson, J. N., and M. F. Willson. 1978. Disturbance and the dispersal of fleshyfruits.Science 200:1161-1163. 1979. Evolution of temperatefruit/bird interactions.Evolution 33:973-982. This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions COEVOLUTION OF FRUITING PLANTS AND FRUGIVORES 413 Van der Pijl, L. 1972. Principlesof dispersal in higherplants. Springer-Verlag,New York. Williams,G. C. 1975. Sex and evolution. PrincetonUniversityPress, Princeton,N.J. Willis, E. 0. 1966. Competitive exclusion in birds of fruitingtrees in Western Colombia. Auk 83:479-480. . 1974. Populations and local extinctionsof birds on Barro Colorado Island, Panama. Ecol. Monogr. 44:153-169. This content downloaded from 139.140.232.150 on Tue, 24 Dec 2013 11:41:24 AM All use subject to JSTOR Terms and Conditions
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