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1068 ShortCommunications [Auk, Vol. 115 The Auk 115(4):1068-1071, 1998 Competition for Nest SitesBetween Kelp Gulls (Larusdominicanus)and Terns (Sterna maxima and S. eurygnatha)in Patagonia FLAVIO QUINTANA 1 AND PABLO YORIO 2CentroNacionalPatag6nico, CONICET,Boulevard Browns/n 9120,PuertoMadryn,Chubut,Argentina;and WildlifeConservation Society, NewYork,NewYork10460,USA Seabirdsfrequentlynestin mixed-species colonies quantifytheir temporaland spatialpatternsof set(Burger 1985).Severalstudieshave showndiffer- tlement, describeand quantify gull aggressivebeencesin habitat and nest-siteuse amongseabirds havior toward terns, and determine the allocation of (Buckleyand Buckley1980,Croxall and Prince1980, nesting space as a result of spatial interactions Fasola and Canova 1992). However, some degree of amongthesespecies. overlapin habitatand nest-siterequirementsmay Study area and methods.--PuntaLe6n (43ø04'S, existbetweenspecies,resultingin interspecific com- 64ø02'W)is located10km southof the mouthof Golpetitionthat oftenleadsto nest-sitedisplacement or fo Nuevo,Chubut,Argentina.The coastin this area even the replacementof one speciesby another is characterizedby gravel beacheswith extensive (Buckleyand Buckley1980,Burger1985).Spatialin- cliffs30to 100m high.A siltplatformseawardof the teractions between seabirds can be more intense in cliffs and coveredby vegetation(mainly Suaedadi- areaswherehabitatis limited or when the popula- varicata,Atriplexlampa,and Lyciumchilense) is usedas tion of oneof the species is expanding(Burgerand a nestingsite by severalseabirdspecies,including Shisler1978,Trivelpieceand Volkman1979,Duffy Kelp Gulls (6,500 pairs), Royal Terns (650 pairs), 1983, Ainley 1990). At manymixedcoloniesof larids,largerspecies of- Cayenne Terns (1,150 pairs), Imperial Cormorants (Phalacrocorax atriceps;2,650 pairs), NeotropicCor- tendisplacesmallerspecies fromtheirterritories, oc- morants(P.olivaceus; 100pairs),RockShags(P.macasionallyforcing them to abandonthe breeding gellanicus; 1 pair), and Guanay Cormorants(P.bouarea (Burgerand Shisler1978,Burger 1985).In addition, larger larids generallyarrive at breedingsites earlier(MorrisandHunter1976,Burger1985),which gives them a competitiveadvantageover smaller species.Gulls (Larusspp.)frequentlyhavebeeninvolved in the displacement of other speciesfrom breedinghabitats(Thomas1972,Burger1979,Bradley and Monaghan1986, Furnessand Monaghan 1987).Ternsappearto be one of the mostaffected seabirds,andsometernpopulations havedecreased asa resultof populationexpansion by gulls(Thomas 1972,Nisbet 1973,Greenhalgh1974,Courtneyand Blokpoel1983,Parnellet al. 1988,Ainley and Hunt 1991,Blokpoeland Scharf1991). At Punta Le6n, Argentina, Royal Terns (Sterna maxima)and CayenneTerns(S.eurygnatha) breedintermingledin a denseclusterof nestswithin a Kelp Gull (Larusdominicanus) colony.The Kelp Gull colony increasedin size from 3,200 pairs in 1982 to 6,500 in 1995, and gulls currently occupyalmostall of the availablenestingspace(Yorioet al. 1994).Given the overlapin nest-siteuse and the currentex- pansionof KelpGulls,we expected thatcompetition for nestingspacecould result in negativeeffectson both speciesof terns.In this paper,we document spatial interactionsbetweenKelp Gulls and Royal and Cayenne terns at Punta Le6n, Patagonia.We E-mail:[email protected] Addressfor correspondence. gainvillii;2 pairs;numbersfrom Yorioet al. 1994). During 1990to 1992,we obtainedinformationon temporaland spatialsettlementpatternsof Royal Terns,CayenneTerns,and Kelp Gulls.Todetermine settlementpatternsby terns,we countedthenumber of nestseverytwo to threedaysfrommid-September to earlyNovember,usingspottingscopes(20to 45X ) from an observation point on the cliffs 50 to 70 m fromthecolony.Wemonitoredthe growthof thecolonyby mappingits sizeandshapeat intervalsof two to fourdays.Weobtainedsettlementpatternsof Kelp Gulls from late August to mid-Novemberthrough weekly countsof breeding individuals at a study area closeto the tern colonyand during 1990 and 1991by monitoring53 and 40 markednests,respectively,everytwo to threedays.The 20 x 20 m study area used to monitor gull settlementwas locatedin the southernpart of the KelpGull colony. To studythe effectsof Kelp Gull territorialbehavior on tern settlement,during 1990we conducted23 one-hourobservations during whichwe scannedthe colonyfor settlingterns (n 73 groups).When a group of settling terns was detected,we recorded whetherthe ternswere attackedand whetherthey were totally or partially displaced by territorial gulls. We defined "settling terns" asa variablenumber of birdsof bothtern speciesthattried to settleat the colonyperiphery.Mostpairsof ternsbuild nests andlay theireggson the samedaythat theysettlein the colonysite (Quintanaand Yorio1997).We de- October1998] ShortCommunications fined"settledtern"asanybird sittingona nest,with or without eggs.We defineda gull "attack"as any behaviorconsistingof a shortchaseby a peripheral territorialgull (and on occasiona peckwithoutestablishingphysicalcontact)thatresultedin theflight of the groupof settlingternsor of an incubatingtern adjacentto that gull territory.We defineda peripheral territorialgull as any bird holdinga territory, 1069 20 • with or without a nest, located at a distance of less than 3 m from the tern colony. To quantifyKelpGull territorialbehavior(gull ato tacks)towardterns,we madeobservations with spottingscopes andbinoculars fromtheobservation point on the cliff throughoutthe daylighthours (0700 to 2100EST)duringmostoftheternbreedingcycle.Dur- ingeachhour(n = 307),we quantified therateofgull attacksdirectedatsettlingor incubatingterns.During 1991and 1992,we analyzedthe differencein territorial behaviorbetweengullsnestingnearsettlingterns versusthosenestingnearsettledterns. To documentthe displacement of nestingpairsof Kelp Gulls by settlingterns,we monitoredat twodayintervals38and40gull pairsbreedingat thetern colonyperipheryduring1991and1992,respectively. Duringeachnestcheck,we recordedthepresence of gulls at the nest,the stateof the breedingcycle,and the estimateddistanceof the nestto the tern colony periphery.If the gull nestdisappeared(lossof nesting materialandeggs),we recordedwhetherthesite was occupiedby a nestingtern. Results.--KelpGulls settled at the colonyover a two-monthperiod (Yorioet al. 1994).Gulls arrived at the colonyand selectedterritoriesthat were dis- 0 I I I I I I I I 1 2 3 4 5 6 7 8 Week of the breeding cycle FIc. 1. Seasonalvariationin rate of Kelp Gull attacks (• + SD) on Royal Terns and CayenneTerns during1990(week1 = 18to 24October),PuntaLe6n, Patagonia. in the direction of vegetatedground and in areas withoutgull territories. Wedid notquantifygullnesting densitiesat the time of tern settlementto avoid disturbanceto gulls and terns.However,qualitative observations showedthatduringall years,sections of thegull colonyhad lowernestdensities thanthesec- persedthroughoutthearea.Latearrivalssettledbe- tionswhere ternsbred. Moreover,during 1991,terns tweenexistingterritories.Kelp Gull nestingdensity was variable,ranging from 0.002 to 0.75 nests/m2 (Yorioet al. 1994).Colonyformationby Royal and Cayenneternswasinitiatedby a groupof about100 changed thelocation oftheircolonytoanareaofhigher gull densitythanthatusedin thepreviousseasons. Thisnewareahadoneof thehighestnestingdensities of KelpGullson theentirecolony(0.50nests/m2; Yorio et al. 1994).Ternscontinuedto breedin thispartof the colonyfor the nextthreeyears. to 150 individuals that settled on available bare groundamongKelp Gull nests,and the colonygrew throughthesettlementof newgroupsofbothspecies at the colonyperiphery(Quintanaand Yorio1997). The resultingnestingdensityfor both tern species combinedrangedbetween9 and 11 nests/m2 (Yorio et al. 1994).Duringall studyyears,KelpGullssettled The settlementof tern groups(g = 25.7 individuals,range5 to 120,n = 73) at thecolonywasaffected by the presenceof territorialKelp Gulls,with and withoutnests,at theperipheryof thecolony.During 1990,79.4%(n = 73) of the tern groupsthat we folmore than a month earlier than the terns. Gulls startlowedduringsettlement wereattacked by peripheral ed claimingterritoriesduring late Augustand early gulls. Attacks by Kelp Gulls frequently forced September, but bothternspeciesdid notsettleat the groupsof settlingternsto take flight, on occasion colonysiteuntil thesecondor third weekof October. causingthe group to leavethe colony.Of 58 groups However,given the asynchronyin timing of breed- that were attacked, 31% were forced to leave the site ing,someKelpGull pairssettledadjacent to thetern and53.4%werepartiallydrivenawaybygullsby the period.In 15.6%of the cases, colonyduringand afterthe tern layingperiod.Both end of the observation gulls and ternsstartedlaying in mid-October(Yorio we could not determine the results of the interaction. et al. 1994, Quintana and Yorio 1997). The mean numberof Kelp Gull territorial attacks AlthoughKelpGullssettledin the nestingareabe- per hourtowardterngroupswas13.8+ SD of 8.8 (n foretheterns,bothternspecies wereableto establish = 121)in 1990.The numberof attacksper hour deandbreedamonggull territoriesin all threeseasons. creased significantly as the season progressed The growthof theterncolonythroughthesettlement (Spearmancorrelation,rs= -0.98, P < 0.01;Fig. 1). betweengullsandternsocof groupsofbirdsat thecolonyperipherywasmainly Mostspatialinteractions 1070 ShortCommunications [Auk,Vol. 115 Le6n exhibitoverlapin habitatuse (Quintanaand Yorio 1997),and the larger Kelp Gulls arrive at the []Settling terns colonyearlier, Royal Ternsand CayenneTernswere [] Settedterns able to form breeding coloniesby displacingthe gulls. Aggressivebehavior by Kelp Gulls toward terns seems to be related to defense of breeding space,as suggestedby the significantlyhigherrate of attackstoward settlingversussettledterns. The settlementand nestingstrategiesof Royal Ternsand CayenneTernsappearto be important determinantsof competitiveinteractionswith gulls. Althoughlargebodysizeand earlytimingof settlementcanbe importantdeterminantsof the outcome of spatialinteractions(Burgerand Shisler1978,Duffy 1983, Burger 1985), settlementin dense groups may allow smallerbirdsto displacelarger and earlier settlingbirdsthatnestat lowerdensities(Burger 1985). At Punta Le6n, Royal Terns and Cayenne Terns settle at the colonyin relatively large and densegroupsthat are ableto displacenestingKelp Gulls. Similar observations havebeenreportedfor other tern species,suchas SandwichTerns(Sterna 1991 1992 sandvicensis) nestingwith Black-headedGulls (Larus Year ridibundus; Taverner1970,Smith1975,Veen1977),Elnestingwith Heerman's FIG. 2. Rate of Kelp Gull attacks(• -+ SD) toward egantTerns(Sternaelegans) settling and settled Royal Ternsand CayenneTerns Gulls (Larusheermanni;Barrie 1975),and Arctic Terns (Sternaparadisaea) nestingwith Herring Gulls (Larus during 1991and 1992, Punta Le6n, Patagonia. argentatus; Bianki 1977).In this respect,the nesting traitsof the crestedtern groupgivetheman advancurredduringthe periodof ternsettlement,and the tageoverothertern species,manyof whichare or highestrate of gull attackswasduring the first two havebeenaffectedasa resultof expanding gullpopweeksof the terns' breedingcycle(Fig. 1). The av- ulations(Thomas1972,Nisbet 1973,Courtneyand eragenumberof gull pecksandchases per hourdur- Blokpoel1983,Ainley and Hunt 1991,Blokpoeland ing 1991 and 1992 was significantlyhigher toward Scharf1991). settlingthan settledterns(Wilcoxontest;1991,Z = Even thoughwe found no evidencethat terns at 3.43, P • 0.001;1992,Z = 4.56, P • 0.001;Fig. 2). Punta Le6n currently are affected by spatial comEventhoughsomeKelpGull pairsalsosettledafter petitionwith KelpGulls,an increasein gull nesting ternshadselected thecolonysite,gullswereneverob- density due to population expansionmay interfere serveddisplacingternsthathad alreadylaid eggs.In with ternsettlement in thefuture.In addition,Royal only a few occasions, gull territorial behaviorforced Ternsand CayenneTernsmay pay a costby nesting an incubatingternto leavetheeggexposedforseveral amongKelp Gulls owing to delayedbreeding,enerminutes.In contrast,gull territoriesthat had nests, gy lossfrom territorialbehavior,and/or prolonged someof themwith eggs,weretakenoverby settling exposureof eggsduring territorialinteractions.Any ternsduringall threeyearsof thestudy.In 1991and such costsprobablywill increasewith increasing 1992,28.9%(n = 38) and 20% (n = 40), respectively, densitiesof nestinggulls.During 1991,for example, oftheKelpGullpairsnestingin thevicinityofthetern the locationof the terncolonychangedto an areaof colonylosttheirterritoriesandneststo settlingterns. highergull density.Duringthat season, the growth Gull nestdisplacement occurredas the tern colony of the tern colonywasslowerthan in previousseagrew and groupsof settling terns intruded into the sons (Quintana and Yorio 1997). Unfortunately,it territoriesof gulls,takingoverthe nestingspace.On cannotbe determinedwhether the delay in settleoccasion,Kelp Gull nestswere graduallysurrounded ment was a direct consequenceof territorial interby ternpairs,andincubatinggullsretainedtheirnests actions between gulls and terns, a result of lower for sometimebeforeabandoning them.Displacement food availability,or a combinationof thesefactors. of nestinggullsby ternsoccurredevenaftergullshad Giventhepotentialnegativeeffectsonternsof aninstarted laying eggs.During 1991 and 1992,54.5% (n creasein nestingdensitiesof Kelp Gulls, we recom= 11)and87.5%(n = 8), respectively, of thedisplaced mendtheestablishment of a monitoringprogramto gullshadalreadystartedlayingbeforetheyweredis- allow the early detectionof conflictsbetweenthese placed. species. Discussion.--Even thoughgullsand ternsat Punta Acknowledgments.--We thank the Wildlife Conser- October1998] ShortCommunications vationSocietyand WilliamConwayfor the support that allowed us to conductthis study. The project wassponsored by Fundaci6nPatagoniaNatural.We thank Gabriela Aguilar, Marcelo Bertellotti,Laura Biscayart,LucianaChiesa,Mariana Lanfiutti,Cynthia Padula, Fabian P•rez, and Cecilia Ramirez for 1071 and competitive interactionsof Herring and Laughinggullsin New Jersey.Auk 95:252-266. COURTNEY,P.g., AND H. BLOKPOEL.1983. Distribution and numbers of Common Terns on the low- er Great Lakes during 1900-1980:A review. Colonial Waterbirds 6:107-120. J.P.,ANDP.g. PRINCE.1980.Food,feeding helpwith fieldwork.Drs. BernieTershyand Burney CROXALL, ecologyandecological segregation of seabirdsat Le Boeufmadehelpfulcommentson earlierversions SouthGeorgia.BiologicalJournalof theLinnean of the manuscript.We thank the OrganismoProvinSociety14:103-131. cial de Turismo,Chubut, for permitsto work at the Punta Le6n Reserve,and Centro Nacional Patag6n- DUFFY,D.C. 1983. Competition for nesting space amongPeruvianguanobirds. Auk 100:680-688. ico (CONICET) for institutionalsupport. FASOLA,g., AND L. CANOvA. 1992. Nest habitat se- lectionby eight syntopicspeciesof Mediterranean gulls and terns. Colonial Waterbirds15: LITERATURE CITED 169-178. AINLEY, D. G. 1990. Farallon seabirds: Patterns at the communitylevel.Pages349-380in Seabirdsof the Farallon Islands: Ecology,dynamics,and structure of an upwelling-systemcommunity (D. G. Ainley and R. J.Boekelheide, Eds.).Stanford UniversityPress,Stanford,California. AINLEY, D. G., AND G. L. HUNT, JR. 1991. Status and conservationof seabirds in California. 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BURGER, J., AND J. SHISLER.1978. Nest-site selection AssociateEditor: J. Ekman