Nordic Society Oikos The Effect of Plant Density on Departure Decisions: Testing the Marginal Value Theorem Using Bumblebees and Delphinium Nelsonii Author(s): Donald A. Cibula and Michael Zimmerman Source: Oikos, Vol. 43, Fasc. 2 (Jul., 1984), pp. 154-158 Published by: Wiley on behalf of Nordic Society Oikos Stable URL: http://www.jstor.org/stable/3544763 . Accessed: 16/09/2014 11:12 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]. . Wiley and Nordic Society Oikos are collaborating with JSTOR to digitize, preserve and extend access to Oikos. http://www.jstor.org This content downloaded from 130.15.101.145 on Tue, 16 Sep 2014 11:12:47 AM All use subject to JSTOR Terms and Conditions OIKOS 43: 154-158.Copenhagen 1984 The effectof plantdensityon departuredecisions:testingthe marginalvalue theoremusingbumblebeesand Delphinium nelsonii Donald A. Cibula and Michael Zimmerman Cibula,D. A. andZimmerman, M. 1984.The effect ofplantdensity on departure decisions:testingthe marginal value theoremusingbumblebees and Delphinium nelsonii.- Oikos 43: 154-158. The discrete,stochasticanalog of the marginalvalue theorempredictsthat bumblebees shouldrespondto increasesin interplant distanceby increasing the wastestedusing Thisprediction ofopenflowers percentage visited perinflorescence. Bombusflavifrons workers fornectarin naturally of foraging occurring populations nelsonii. Resultssuggest thatbumblebees Delphinium as predicted toreducrespond tionsin plantdensity. bees compensated However,underexperimental conditions, forpotentially costsbyvisiting highflight relative neighboring plantswithincreased thusreducing actualflight frequency, Thisresultsuggests thatbumblebees expenses. butrather, maynotassessflight costsdirectly, useplantdensity toestimate potential costs.At times,thismethodof assessment foraging of couldyieldan overestimate in sub-optimal foraging costs,resulting decisions. departure D. A. Cibula, Dept of Biology,SyracuseUniv.,Syracuse,NY 13210, USA. M. Zimmerman(correspondence),Dept of Biology, Oberlin College, Oberlin,OH 44074, USA. cToxacTmqecKmttaHaJOlrTeopem KpaeBOR BemImHHi flpegCKa3aJI iyBCT,1HcKpeTHbK9 K yBeThIUeHHmS BHTefbHOCTh u*ete paCCTmHHRWezQo pacTeHHH, rIpo~nvLantio-C3H B IIOb1bxHM4 rpOeHTa OTKqlTIND uBeTKoH, mCHa QoHcm aouv ixteTHH. ,nOCcA c namouuEjo 39roripeciKa3aae npoBepsm pa6oHx ooo6en Bombusflavifrons co6IpaEmxm HeKTap Ha r p~ ~c onyoryxsrssx Delphiniumneisonji. Pe3yxbTam fIOTHoxiTO IvIemEpeampyo, nOKa3a&rxH, KaK 6E: rIqrCKa3aHO, Ha CHmeKeHHe cTm pacTeHmi. 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Wa TecKme Accepted 14 September 1983 OIKOS ? 154 OIKOS 43:2 (1984) This content downloaded from 130.15.101.145 on Tue, 16 Sep 2014 11:12:47 AM All use subject to JSTOR Terms and Conditions Introduction Many animals utilize resources that occur in discrete clumpsor patches.An animal thatvisitsmanypatches duringa foragingbout mustcontinuallydecide whether to remainin the presentpatchor move to another.One of the questions optimal foragingtheoryattemptsto answer is: how long should a foragerremain in each patchin orderto maximizeits rate of net energyintake (RNEI)? Charnov (1976) addressed this question from a theoretical standpoint and developed the marginal value theoremto predictwhen an optimallyforaging animalshouldleave a givenpatchand move to another. The model assumesthatby feeding,a foragerdepresses theavailabilityof food in a patch(Charnovet al. 1976), thus lowering its RNEI below what it could have achieved by an earlier move to anotherpatch. But, if movesare made too soon too muchtimeand energyare spenton interpatchtravelyieldinga sub-optimalRNEI. A numberof testsof the marginalvalue theoremhave been carriedout (Krebs et al. 1974, Cowie 1977, Pyke 1978a, 1982, Heinrich 1979, Hodges 1981, Zimmerman 1981a, Best and Bierzychudek1982) and, in general, resultsare consistentwithits predictions. The marginalvalue theorem,as formulatedby Charnov (1976), is only applicable to a systemin whichan and continuanimal'sRNEI decreasesdeterministically ously withtime spent foragingin a given patch (Pyke 1978a). Pyke (1978a, 1981) modifiedthe model,makingit applicable to a discrete,stochasticsystemsuch as animals foragingfor nectarin patches of flowers(e.g. inflorescences).In this case, food occurs at fixed,discrete points(i.e. flowers)on an inflorescence,and the amountof energyobtainedat any flowermaybe correlated with the amount of energyobtained at a previouslyvisitedflower(Pyke 1978a). The pertinentquestion is thus how many flowersper inflorescencean optimallyforaginganimal should visit,not how long it should stayon each inflorescence. The average RNEI for the habitat is a functionof timeand energycostsof interpatchmovementand thus changesin thesecostsaffectdeparturedecisions(Cowie 1977). As costs of interpatchmovementincrease,the discrete, stochastic analog of the marginal value theorem predicts that an optimallyforaginganimal should visit more flowersper patch because of three related variables. 1) As the distancesbetween flower patchesin a givenhabitatincrease,a foragermaytravel greaterdistances when movingbetween patches and, thus,incurincreasedforagingcosts(Waddington1980). 2) If otherfactorsremainconstant,an increasein these costs should resultin a decrease in the average RNEI forthe habitat.3) As thisrate is lowered,therewillbe an increasein thenumberof flowerswithinanypatchat whichthe expected RNEI exceeds the overall habitat rate. The purpose of our researchwas to test thisdeparture prediction with Bombus flavifronsworkers foragingin a naturallyoccurringpopulation of Delphiniumnelsoniiwhosedensityhas been experimentally manipulated. D. nelsonii is an ideal species for this test because resource presentationmeets all of the criteriaof the discrete, stochastic version of the marginal value theorem.It is an herbaceousspecies bearingflowerson a singleverticalinflorescence.Thus, each plant or inflorescencemay be consideredto be a single,discrete patch.There is a negativecorrelationbetweenheightof a floweron the raceme and standingcrop of nectar (Pyke 1978b). Bees exhibitstereotypicbehaviorwhen foragingon thisspecies,commencingat bottomflowers and movingup the verticalinflorescence(Pyke 1978b). Given these nectarpatternsand systematicbee movements,it is possible forbees to estimatethe RNEI expected fromany floweron an inflorescence.It is thus expected that bees foragingfor nectar on D. nelsonii could use the departurerule predictedby the discrete, stochasticanalog of the marginalvalue theorem.Such behavior would be consistentwith previous studies workersflying showingthatB. flavifrons between(Pyke 1978c), as well as within(Pyke 1979), D. nelsoniiinflorescencesare, in fact,foragingoptimally.In addition, Hodges (1981) and Zimmerman(1983) have shown that the departure decisions made by B. flavifrons workersin responseto the standingcropsof nectarencounteredon D. nelsonii inflorescencesare consistent withpredictionsfromoptimalforagingtheory. Methods Fieldworkwas conductedduringJuneand July,1980, at Kebler Pass (elevation 3048 m a.s.l.), a montane meadow in Gunnison National Forest, 11 km W of CrestedButte,Colorado. A 20 m2studyplotwas establishedin a dense populationof D. nelsonii.All D. nelmarkedby sonii plantswithintheplot were distinctively tyingcoloredpieces of embroiderythreadto theirstems and theirlocationswere mapped. The numberof open flowerson each inflorescencewas countedeveryother day. B. flavifronsworkerswere observed as theyforaged for nectar withinthe studyplot. As a bee flew from plantto plant,the color codes of visitedplantsand the numberof flowersvisitedwere recorded.Using plant maps and flowercensus data, foragingbouts were recreated and the percentageof open flowersvisitedper plant,flightdistances,nearestneighborstatusof visited plants and interplantspacing distances were determined.Interplantdistancewas measuredas thedistance betweena plant and the nearestnonspecificindividual havingat least one open, available flower.The nearest neighborstatusof a visitedplantindicateswhetherthat plant was the closest or second, third,etc., closest neighborof the plantjust visited. The experimentwas dividedinto threephases. Dur155 OIKOS 43:2 (1984) This content downloaded from 130.15.101.145 on Tue, 16 Sep 2014 11:12:47 AM All use subject to JSTOR Terms and Conditions ing phase I, foragingbouts were observedundernaturally occurringplant densities.During phase II, density of D. nelsoniiwas reduced by randomlybagging(with nylonnetting)a fractionof thepopulation.Because the nettingpreventedbees fromvisitingflowers,bagged plantswereconsideredto have no available flowersand were not censused duringthis phase. Foragingbouts were observed underthisexperimentally reduced density.All plantswere thenunbaggedand again,foraging bouts were observed(phase III). Results Bagging plants reduced densityby 51.8% relativeto phase I and 42.7% relativeto phase III. The mean interplantdistances (Tab. 1) differsignificantly among phases (k-samplevan der Waerdentest(Marascuiloand McSweeney 1977); W = 6.36; 2 df; P = 0.042; N = 395). Mean interplantdistanceforphase II is significantlygreaterthan thatforphase I, but is not significantly greater than the mean for phase III (Tab. 1). Contraryto the design of the experiment,unbagging plants did not quite restore plant spacing to their originalvalues. Flower mortality over the courseof the studyreduced plantdensityand resultedin non-significantdifferences in interplantdistancesbetweenphases II and III. The percentageof open flowersthatbees visitedper plantis notindependentof plantsize (i.e. thenumberof open flowerson a plant)(X2= 24.87; 4 df;P < 0.005; N = 145). A testfortrendshows thatbees visitedhigher percentagesof flowerson small plants than on larger plants.The percentageof open flowersvisitedper plant at Kemeasured Tab. 1. Meansandsamplesizesforvariables blerPass. 0 withplantsize( = 0.430; decreasesmonotonically x2 = 22.61; P < 0.005; N = 145). Departurefrom is notsignificant monotonicity (X2= 2.26; 3 df; P > 0.10; N = 145).Themeansizeofvisited plants(Tab. 1) differs significantly amongphases(k-samplevan der Waerdentest;W = 6.62; 2 df;0.05 > P > 0.025; N = as a covariate andanalysis 148) so plantsizewastreated ofcovariance wasusedto determine whether themean of open flowersvisitedper plantdiffered percentage amongphases.Variancedue to sizeclasswasremoved priorto determining variancedueto interplant distance (themaineffect). The mean percentage of open flowersvisitedper plantdiffers significantly amongphases(Tab. 2). As wasdepredicted, duringphaseII, whenplantdensity creasedand interplant distancesweresignificantly increased,beesvisiteda greater ofopenflowpercentage ers per plant relativeto both controls(StudentNewman-Keuls test;P < 0.05). The twocontrols did notdiffer significantly fromone another(Tab. 1). The departure decisionprediction assumesa positive relationship between interplant distance andbumblebee flight distances. DuringphaseII thisassumption wasnot met.Mean flight distancesforphaseII were,in fact, significantly shorter thanthemeansforbothphasesI and III (Tab. 1), implying thatbees flewto nearby plantswithgreater relative frequency during phaseII. A k-sample vanderWaerdentestshowsthatthemeansof the frequency distributions of the nearestneighbor statusof visitedplants(Tab. 1) differsignificantly amongphases(W = 8.63; 2 df;0.025 > P > 0.01; N = 122). A posteriori testsindicatethatthemeannearest neighbor statusofvisitedplantsforphaseII is significantlysmallerthanthoseforbothphaseI and III. The mean interplant distanceforphase II was, however, substantially greater(30.8%) thanthatforphaseIII, and mayhavebeen largeenoughto trigger thesame responsebybees. Phase I distance(m) Interplant Plantdensity (no. plantsm2) Flightdistance(m) Nearestneighbor status Size (no. openflowers/ visitedplant) Percentflowers visited II III 0.157W 0.120db 0.110' N = 170 N= 82 N= 143 8.50 0.468W N = 65 7.67' N= 63 N= 39 N= 20 3.78 N= 60 3.51 N= 45 3.33 N= 24 42.80a 54.67b 45.65a N = 60 4.10 7.15 0.322b 0.768a N= 39 N= 21 3.03b N= 45 7.55a N= 24 Discussion Bumblebees, as predicted, adjustedtheirdeparture decisionsduringtheexperimental periodin whichplant Tab. 2. Resultsof analysisof covarianceused to testnull hypothesisthatthe means forpercentof open flowersvisited per plant do not differamong phases. Plant size (numberof open flowerson visitedplants) was used as a covariate. Source of variation df SS MS F P Covariate: Plant size .......... 1 0.724 0.724 18.98 0.001 Phase .............. 2 0.369 0.185 4.84 0.009 128 5.863 0.046 Maineffect: Explained.......... a. Different indicatevaluesthatdiffer superscripts between Residual........... phasesat P < 0.05. TOTAL ........... b. 2 1.093 0.364 125 4.770 0.038 156 9.55 0.001 OIKOS 43:2 (1984) This content downloaded from 130.15.101.145 on Tue, 16 Sep 2014 11:12:47 AM All use subject to JSTOR Terms and Conditions reduced,and visitedincreased thoughnot predictedby the marginalvalue theorem, densitywas significantly but it is not percentagesof blossomsbeforeleavingindividualflow- appears to increase foragingefficiency, eringstalks.This resultis in contrastto thatfoundby withoutcost. Because standingcropsof nectaron adjaZimmerman(1981a) who also worked withB. flavi- centD. nelsoniiplantsare positivelycorrelated(Pleasfronsworkersas well as B. bifariusworkers.Zimmer- ants and Zimmerman1979, Zimmerman1981b), visits man (1981a) compared the mean percentageof open to nearbyneighborsafterencounteringa low reward flowersthatbees visitedper plantfortwoplantpopula- inflorescencemay yield additional below-averagerein density.These popula- wards. Thus, the higher flightcosts associated with tions differingsignificantly tionsare 8 km apart and differby 300 m in elevation. longermoves are oftenwell worthpaying.In any case, Contraryto prediction,the mean percentageof open as pointedout by Zimmerman(1981a), the behavioral impliesthat byanimalsstrongly demonstrated be- flexibility flowersvisitedper plantdid not differsignificantly tweenthe two sites (Zimmerman1981a). The cause of those optimalforagingmodels predictinga shiftin any betweenthesetwo studiesis not entirely one particularbehavior in response to environmental the difference clear. UncontrolleddifferencesbetweenZimmerman's conditions are too simplisticto accurately predict study sites may have had confoundinginfluenceson foragingbehavior. It should be pointedout thatrates of nectarproducforagingbehavior. Secondly, the mode of resource presentationon Polemoniumfoliosissimumdifferssub- tion and/orvolumesof standingcrop may have varied stantiallyfromthat on D. nelsonii,possiblyaffecting among experimentalphases. Such a change, however, effecton bumblebee bees' abilitiesto predictfuturerewardson a plant.Un- should not have had a significant like D. nelsonii,resource presentationon P. foliosis- departuredecisions.Ollason (1980) has presentedthe thatdeparture demonstrating simum is non-orderly;flowersappear to be scattered mathematicalverification randomlyover the plants'outer surfaces.Additionally, decisionsare actuallyindependentof theoverallhabitat it is unknownwhetherthecorrelationin nectarvolumes average reward value while Cibula and Zimmerman between adjacent blossoms on a D. nelsonii raceme (unpubl.) have confirmedthatunderexperimentalcon(Pyke 1978b) also occurs on P. foliosissimum.These ditions bumblebees on D. nelsonii (as well as on D. departurerulesforthetwo barbeyiand Aconitumcolumbianum)foragein a manfactorsmaylead to different ner consistentwithOllason's predictions. plantspecies. The behavioral responses observed in the present Althoughthepredictionof the analog of themarginal value theoremwas met duringthe experimentalphase studyalso have some relevanceto the mannerin which of the currentstudy,examinationof anotheraspect of bees assess the costs of foraging.All optimalforaging bumblebee behavior suggeststhat this resultmay, in models assume that animals are constantlycomparing fact,be paradoxical. The predictionthat bees would theirenergeticexpenditureswiththeirenergeticgains visitmore flowersper inflorescenceunder low density and makingmovementdecisionsbased on the ratio of conditionsstemmeddirectlyfromthe assumptionthat thesetwovalues. The currentworkraisesthepossibility flightcosts thatanothermethodexists.Bees maynotestimateflight under such conditionsinter-inflorescence would be increasedrelativeto highdensityconditions. costs directly,but ratheruse an assessmentof plant Larger movementcosts should resultin foragersbeing spacingdistancesas an indexof potentialforagingcosts. less inclinedto leave patches(Cowie 1977, Zimmerman Bumblebee foragingduringphase II is consistentwith 1981a). Despite the fact that plant spacing distances this hypothesis.Upon enteringan area of low plant were greaterduringthe experimentalphase of the pre- density,bees, in an attemptto decrease theirforaging shorterdistances costs,increasetheirfrequencyof moves to near neighsent study, bees flew significantly beforededuringthis phase than duringcontrol periods. If re- bors and visitmoreflowersper inflorescence duced flightdistances indicate lowered inter-inflores- parting.It is possibleforbees to overcompensate,howcence flightcosts (Waddington 1980), the discrete, ever, and this is what appears to have happened in stochasticanalog ofthemarginalvalue theoremactually phase II. Duringthisperiodbees increasedtheirutilizapredictsthat the numberof blossoms visitedper stalk tion of nearestneighborsto such an extentthat their should have been lowest during the experimental absolute flightdistances were actually significantly period. Therefore, because of decreased flightdis- shorterthan duringeithercontrolperiod. The number tances,thisresultimpliesthatbees are notforagingin a of blossoms visitedper inflorescenceduringthis time period,however,was consistentwiththatexpectedhad mannerconsistentwiththe marginalvalue theorem. The shorteningof flightdistances in response to a bees' flightdistancesbeen greaterthan in the control decrease in plant densityis due to the increased fre- phases. If departuredecisionsare based on a visualperquencywithwhichbumblebeesbegan to move between ception of the environmentinstead of on the actual can thuslead to near neighbors.Bees made the same response to low flightcostsincurred,overcompensation sub-optimalforaging.The resultsof the presentstudy densitystandsofP. foliosissimum(Zimmerman198 la). In both cases it appears that changes in plant density suggestthat if bees are basing departuredecisions on triggereda behavioralresponsethatdecreased the cost directlyestimatedcosts,theyare not foragingin keepmovement. This behavior, al- ing withpredictionsof the marginalvalue theorem.If, of inter-inflorescence 157 OIKOS 43:2 (1984) This content downloaded from 130.15.101.145 on Tue, 16 Sep 2014 11:12:47 AM All use subject to JSTOR Terms and Conditions on theotherhand,bees estimateforaging costsindi- Krebs,J. R., Ryan,J.C. and Charnov,E. L. 1974. Huntingby expectationor optimalforaging?A studyof patch use by rectly via plantdensity, foraging modelsneedto be rechickadees.- Anim. Behav. 22: 953-964. formulated to incorporate thisbehavior.Clearly,tests Marascuilo,L. A. and McSweeney,M. 1977. Nonparametric needto be designedthatare capableofdistinguishing and distribution-free methods for the social sciences. Wadsworth,Belmont,CA. betweenthesetwomethodsof decision-making ifthe efficiency of bumblebeeforagingand the utilityof Ollason, J.G. 1980. Learningto forage- optimally?- Theor. Pop. Biol. 18: 44-56. optimalforaging modelsare to be evaluated. Pleasants,J. M. and Zimmerman,M. 1979. Patchinessin the dispersionof nectarresources:Evidence forhot and cold spots.- Oecologia (Berl.) 41: 283-288. Pyke,G. H. 1978a. Optimal foragingin hummingbirds: Testingthemarginalvalue theorem.- Am. Zool. 18: 739-752. - We are indebtedto A. Frucht,R. Gross Acknowledgements - 1978b. Optimal foragingin bumblebees and coevolution and J.Pleasantsformakingneeded improvements in an earlier withtheirplants.- Oecologia (Berl.) 36: 281-293. draftof this manuscript.This study was supportedby NSF - 1978c. Optimal foraging: Movement patterns of grantsDEB 80-04280 and DEB 81-01800 and bya grantfrom bumblebees between inflorescences.- Theor. Pop. Biol. the Societyof Sigma Xi. We appreciatetheirsupport. 13: 72-98. - 1979. Optimalforagingin bumblebees:Rule of movement - Anim.Behav. 27: betweenflowerswithininflorescences. 1167-1181. - 1981. Optimal foragingin nectar feeding animals and coevolution with their plants. In: Kamil, A. C. and References Sargent,T. D. (eds), ForagingBehavior. Garland Press, Best, L. S. and Bierzychudek,P. 1982. Pollinatorforagingon New York. foxglove(Digitalispurpurea): A test of a new model. - 1982. Foragingin bumblebees:Rule of departurefroman - Can. J. Zool. 60: 417-428. Evolution36: 70-79. inflorescence. Charnov, E. L. 1976. Optimal foraging:The marginalvalue Waddington,K. D. 1980. Flightpatternsof foragingbees relatheorem.- Theor. Pop. Biol. 9: 129-136. tiveto densityof artificialflowersand distribution of nec- , Orians,G. H. and Hyatt,K. 1976. Ecological implications tar.- Oecologia (Berl.) 44: 199-204. of resourcedepression.- Am. Nat. 110: 247-259. Zimmerman,M. 1981a. Optimal foraging,plant densityand Cowie, R. J. 1977. Optimal foragingin great tits (Parus the marginal value theorem. - Oecologia (Berl.) 49: major). - Nature,Lond. 268: 137-139. 148-153. - 1981b. Patchinessin the dispersionof nectar resources: Heinrich,B. 1979. Resource heterogeneityand patternsof movementin foragingbumblebees. - Oecologia (Berl.) 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