1387 Postemergence northern turtle, behaviour peripheral .Abstract: .: population Emydoidea K. Lorraine Standing, Ian P. Morrison of neonates of Blanding's blandingii, Thomas in a in Nova B. Herman, Donna Scotia D. Hurlburt, and The early postemergencebehaviourof neonateBlanding's turtles, Emydoideablandingii, was studied in Nova Scotia in 1994and 1995to test the hypothesisthat hatchlingsgo to water immediatelyupon emergencefrom the nest. At the northeasternlimit of the species'range,hatchling turtles should seekaquatichibernaculato avoid freezing; where emergencefrom the nestis delayeduntil late autumn, selectionpressurefor water-seekingbehaviourshould be strong. Using pigmentedpowder that fluorescesunder UV light, 78 hatchlingsfrom 12 lakeshorenestsand 2 inland " nestswere tracked for a maximumof 11 days. On the first day after emergence,hatchling movementwas random with respectto water. Hatchlingsdid not orient themselveswith respectto slope, vegetation,or nestmates,nor did individuals follow a consistentcompassbearing amongdays. Often trails were convolutedin the openand relatively straight underdensevegetation.Evidencesuggeststhat hatchlingsin this populationmay overwinter in terrestrial as well as aquatichibernacula. Resume: Le comportementde Tortues mouchetees,Emydoideablandingii, fraichementemergeesdes nids a ete etudie enNouvelle-Ecosseen 1994et 1995pour eprouverl'hypotheseselonlaquelleles petitestortuesgagnentl'eau immediatement apres leur sortie du nid. A la limite nord-estde la repartitionde l'esp"ece,les petitestortues devraienttheoriquementse chercherdes hibernaculumsdans l'eau pour echapperau gel; la oil l'emergencedu nid est retardeejusqu'a la fin de l'automne,la pressionde selectionqui favorise Ie comportementde recherchede l'eau devrait logiquementetre forte. La trajectoire de 78 tortues neonatesa ete suivie durant un maximumde 11 jours a partir de 12 nids sur les rives et de 2 nids loin des rives, par utilisation d'une poudre pigmenteefluorescentea l'ultra-violet. Au ler jour de I'emergence, la trajectoire des tortues etait aleatoire par rapport a la positionde l'eau. Les tortues ne s'orientaientni en fonction de la pente, ni en fonction de la vegetationou par rapporta leurs congeneres,et aucunetortue n'a suivi une trajectoire selon une direction geographiquedefinie pendantplusieursjours. Les trajectoiresetaientsouventcirconvolueesen terrain ouvert et relativementrectilignessousla vegetationdense.II sembleque les tortues neonatesde cette population puissentpasserl'hiver dansdes hibernaculumsterrestresaussibien que dansdes hibernaculumsaquatiques. [Traduit par la Redaction] Introduction Blan dmg ., f res h wa th f cally reproductive females. The paucity of information on turtl t s er species th G (E .. e my , 7 wes em ova th WI t L k sou 0 e rea th t N sou th d .d 01 ea a narrow Th a es. S t. co bI. la, a nd a ." mgll ) 1 t ' t d. al a all e sm t th e no " th N ' IS I u m d " a W ew range t Id t or cen ere 1 t " d , IsJunc popu a Ion m rth t t .t f eas em d '" ex reml yo. 1993 b th young turtles makes it difficult to protect the younger, more . vulnerable age-classes effectIvely. Consequently, we have ... directed h.. f E b ' nd..., N S . IStOrystrategies 0 , ta mgll m ova cotIa. our research efforts at understandmg the early lIfe .. mformatlon especles range, was ecare y e C ' tt th Stat f E da reaene d W ' ldl m ' ti ' c ana d omml ee on e us 0 n ngere I I e m a (Herman et al, 1995). The resulting Recovery Plan for the th 1 l.ti h. fE bl on e ear y I e IStory 0 .an poI?~lation (Herman et al,)2 identifies research priorities to facIl!tate man~g~~ent. As part of the~e effort~ sever~ studies were mltIated (McMaster 1996; McNeIl 1996; Mockford 19965; I,P. Morrison and K,L, Standing, in preparation), Despite these recent contributions, our understanding is primarily restricted to adult age-classes,specifi- 2 T.B. Herman,J.S. Bleakney,J.S. Boates,J. Dickie, C, Drysdale,J. Gilhen, I. Morrison, T. Power, and K.L. Standing. National RecoveryPlan for the Blanding's Turtle (Nova Scotia Population),Recoveryof Nationally EndangeredWildlife Committee,Ottawa, OntoSubmittedfor publication. 3 McMaster, N,L. 1996. Age structure, distribution, habitat selectionand movementpatternsof juvenile Blanding's turtles (Emydoideablandingii) in Kejimkujik ~ational Park, Nova ., d 1 d t ReceivedNovember 13, 1996. AcceptedMarch 26, 1997. K.L. Standing T.B. , ..'... Herman I and D.D. Hurlburt. Departmentof Biology, AcadIa UnIVersIty,Wolfville, NS BOP lXO C d In M ' , panka ac' da K " mku ' ik N t. al P k ar sana, eJI ~ a Ion ar, M.c.. I orrIson. d B .d A I. C ty NS BOTIBO C da alt an n ge, nnapoIS oun , , ana. I Author to whom all correspondence shouldbe addressed (e-mail: [email protected]). Can. J. Zool. 75: 1387 -1395 (1997) As 4 for Scotia: McNeil, many freshwater turtle species, most d ..., I' . mgll IS Imlte d to reports B.Sc. Hons. thesis, Acadia University, Wolfv~lle, J. 1996. Post-emergent movement of hatchlIng N,S, Bl d ., I (E .]..] bl .]. .. (H Ib k» ' an mg s turt es myuoluea anumgll 0 roo m Kejimkujik National Park, Nova Scotia,B.Sc. Hons. thesis, A cad.Ia Umverslty, .. WOle, lfv ' ll N..S 5 M k l' d S 1996 A .. f al I . oc lor" .genetIc comparIson0 sever popuatIons of Blanding'sturtle (Emydoideablandingii). B.Sc. Hons. thesis,Acadia University, Wolfville, N.S. @ 1997 NRC Canada 1388 Can. J. Zool. Vol. 75, 1997 of clutch size and survivorship and hatching success (Herman et al. 1995; Power 1989; MacCulloch and Weller 1988; DePari et al. 1987; Petokas 1986; Congdon et al. 1983; Bleakney 1963; Brown 1927; Snyder 1921). Few studies have investigated the behaviour and habitat requirements of immature E. blandingii (McMaster 1996, see footnote 3; Pappas and Brecke 1992) and virtually nothing is known about hatchlings (McNeil 1996, seefootnote 4; Butler and Graham 1995). To date, the most significant contributions to our understanding of the behaviour and habitat requirements of neonate E. blandingii have been provided by Butler and Graham (1995). These authors concluded that newly emerged hatchlings in Massachusettsmove from their inland nests to wetlands, likely in search of aquatic hibernacula. However, some of their results appear to be at variance with ttIis conclusion, primarily because of ambiguous terminology the location of their stud site (inland) which did not .'. ...~. '. facIlitate mvest!gatlon ?f th.e ~nentatlon "!echarusm, and the s~all saD1plesIze, :whIch lImIted conclusIons at the populatIon level and specIes level. While there are many similarities between the Nova Scotia population and those elsewhere, Herman et al. (1995) and Power (1989) have identified behavioural differences in this northern population. To date, all differences noted are associated with adult behaviour, and it is suspected that they are responses to environmental constraints at the northt I.. t f th ., (H t 1 1995 ,eas ern Imi 0 e specIes range erman ea.. ' P?wer 1989; Bleakney 1958). The POSSI~IlItyofbehavI~ural dIvergence m younger age-classes, partIcularly hatchlIngs, must not be overlooked in the development of management strategies. Since the protection of hatchlings is a crucial component of the successful recovery and stabilization of the E. blandingii population in Nova Scotia (Herman et al., see footnote 2; Iverson 1990), a greater understanding of the early postemergence behaviour of neonates in this northern, isolated population is required. It is generally assumed that hatchling freshwater turtles go to water upon emergence from the nest (Ehrenfeld 1979). However becauseof the limitations of Butler and Graham' s (1995) s~dy and the possibility of behavioural divergence in h hI ...remaining atc figS, we InvestIgated the early postemergence behav...,. loUr of hatchlIngs m the Nova ScotIa populatIon. The unique nesting habits of E. blandingii in Nova Scotia provide ideal cir~u~stances ~or inv.estigating neonate behavlour. Elsewhere m Its range, IncludIng Massachusetts ." .0 (Butler and Graham 1995), thIS specIes typIcally nests Inland and away from open water (Butler and Graham 1995; Ross and Anderson 1990; Petokas 1986; Congdon et al. 1983); the Nova Scotia population is unique in that females tend to nest along cobble lakeshores. Though some females in this population nest inland more than 200 m from open water, the majority nest within 5 m of open water (Power 1989), and though lake levels f1uctuate,hatchlings emerging from beach nests have an unobstructed .' view of the lake. This and the duratIon of the study (two seasons), enabled us to study a large! samp~e.than that of Butler. an? Graha~ (.1995),and to ~rovlde st~tIStIcalas well as qualItatIve deSC~IptIons of hatchlIng behavIour. We were also able to eXaD1memore closely the water-seeking strategies of E. blandingii hatchlings. Our research is intended to complement the work of Butler and GrahaD1(1995), providing further insight into the adaptations of E. blandingii as a species, and the particular adaptations of young turtles in the Nova Scotia population. We reasoned that at the northeastern limit of the species' range, hatchlings should seek aquatic hibernacula to avoid freezing, and that because of late emergence from the nest, selection for such water seeking should be strong. Here we address the explicit hypothesis that hatchlings go to the nearest water immediately upon emergence from the nest. Materials and methods Study site This studywasconductedin Kejimkujik NationalPark, Nova Scotia (44°15'-44°30'N, 65.o00'-65°30'~), during summerand autumn 1994 and 1995: Nestl~g and hatchlIng m?ve~ent data were collectedat~~ majorn~stmgcenter~(asdescr~bed m Power 1989)and at an ad.dltlonalnestIngbeachdiscoveredm 1995.. . Nestmg beacheshave a gradual slope and typically comprIse fist-sizedcobbleand large pebbles.Beachesare sparselyvegetated with grasses, rushes, and cranberry (Vaccinium macrocarpon) (Roland 1945). The upperbeachesare bordered with huckleberry (Gaylussacia baccata), blueberry (Vaccinium spp.), leatherleaf (Chamaedaphnecatyculata), sweet gale (Myrica gale), red and white pine (Pinus resinosa,and P. strobus),and maple (Acerspp.). Inland nestswereconstructedin the gravel shoulderon the north s~deora two-lane pavedroad. .Theshoulderis 2 m wide on both sidesof the road and descendsInto a more steeplysloped bank of mowed vegetation. The lower banks are bordered by a steep forested... InclIne (predominantlyP. strobus). A densemat of saturated Sphagnumspp, (0.5-1.0 m wide) occurs along the base of the south-sideslope. The nearestopen water is a small marsh located north of the road, 100-150 m west of the sampled nest sites. Nestiug and emergence Beachesand roadsideswere surveyed for nesting E. blandingii throughoutJune in 1994 and 1995. Nestswere protected against predationwith a raised wire-meshcageonce nestconstructionwas complete;this cagealso servedas a pen for emergenthatchlings. BeginningSeptem~r I in both years,nestswere ch~~kedregularly for emergenthatchlings.In late Octoberall nestcavitieswere excavatedto determinethe numberof unhatchedeggsand to free any hatchlings. Upon discovery,hatchlingswere measured ( . I th CL) t h d s: .d t. fi t. maximumcarapaceeng, , no c e lor I en I Ica Ion (Stand ing et al. 1995) dustedwith tracking pigment and released. ' , Dusting and tracking d d h. h fl d UV I ' ht (R d. oure power, w IC uorescesun er Ig a Iant C01or, LBRS Series,Richmond,Calif.), wasusedto track emergenthatchlings (Butler and Graham1993). Hatchlingswere dustedusing a cotton swab,covering the carapace,plastronand leg sockets,but particularcarewas takento avoid contactwith the eyesand nostrils (Stapp et al. 1994), Nestmateswere assigneddifferent colours wheneverpossibleso that individual trails could be distinguished du:ing t:acking, Hatchlingsw~re releasedat the nestsite in random onentat~onand were le.ftundisturbed. . C 1 At night, powder trails were follo~ed usm~ hand-held UV lam.ps (Ray tech Raytector) and marked with flaggIng tape secured with pebbles.Flagging tape was superimposedon the entire length of mosttrails, thoughin somecasesit waslaid at intervals. If a hatchling was found at the end of a trail, its locationwas markedand it wasredustedwith the originalpigment.To minimizedisturbanceon suchoccasions,the area immediatelysurroundingthe turtle, rather thanthe turtle itself, was powdered;hatchlingswalked throughthe @ 1997 NRC Canada . \ -, Standing et al. 1389 powderas theyresumedtheir trek, facilitating the collectionof data over severald~ys. ..Scotia Flaggedtrails were mappedusIng a compass(azimuthto the nearestdegree)and a measuringtape or meter stick (to the nearest 0.1 cm). Trails w~r~mappedin relat~onto water, vegetation,topography, nest of OrIgIn,and other trails. Table 1. Orientationof hatchlingBlanding's turtles in Nova with respectto the water nearestto the nest; analyses include first-da routes onl y y. No. of Orientation Angle of Nest hatchlings Distance to nearest Length meanvector T it al .No. ra an YSIS ! , Trail datawere analyzedusing circular statistics(Batschelet1981, 1965; Zar 1984).The V testis usedto testwhethera set of angles tendsto clusteraround a hypotheticaldirection (00). In this study, we wanted to test not only whether hatchling movement (y) is directed (nonrandom),but whetherit is directedtoward water (°0) (Batsche1et 1981).The null hypothesisis thatthe parentpopulation from which the sample(YI' Yz, ..., Yn) is drawn is randomly (uniforrnly~dist~ibutedaboutthe hypotheticaldirection (00). .10" The orlen~tl~n from nest to near~st w.ater was standardized among nests WIthIn years so that the Orientation (y) of the resultant vector (R) of eachhatchling's first-day trek was convertedto the polar angle y': LetYI,Yz, ...,'tnbenobservationsofhatchlingorientation (azimuthclockwise from north) on day 1 from a single nest; let fJ be the direction to the nearestwater from this nest. Rotatingthe originalzero direction (north)so that fJbecomesthe newzero direction, °0 yields the new polar angle 't' from the original 't. The new polar angle is defined by [1] 't' = Y -fJ and its value is eitherpositive or negative,correspondingto either a clockwise or a counterclockwiserotation from 00 (Batschelet 1965). The new sample ('t'I' 't'z, ..., 't'n) for each year was plotted on a unit circle andthe meanvector(m '), its length (r'), and its polar angle «1>')were calculated. Then the componentof the meanvector with respectto the direction to the nearestwater, or "the homewardcomponent" (v), and the test statistic (u) were calculated(Batschelet1981). If the critical value u(a) is less than or equalto the teststatistic (u), the null hypothesisof randomness is rej~ted. To Investigatethe possibilitythathatchlIngswereorgamzedWith respectto somefeatureother thanwater,.a ph.enomenon thatwould be maskedby the Vtest,nestswereexamInedIndependently for patterns in first-day movementamongnestmates. By plotting the original 't samplesseparatelyfor each nestand calculatingthe meanvector (m) and its length (r), the length of the meanvectoris usedas an index of angulardispersionamongnestmates(Zar 1984).Sincethe samplesize (n) within nestsis small, we arbitrarily definednestswith r > 0.6 as "directed." If the polar angle ("') of the meanvectoris in the direction of the nearestwater (fJ), so that [2] IfJ-"'I < 25° .productive, and r > .O.?, then hat~hlmg ~ovement on the firs,t,d.aY after emergence WIthIn the nest IS considered to have been dtrected toward th t e neares t wa " er. To assessthe straightnessof anindividual's courseamongdays, the resultantvector (R") and correspondingangle ('t") of each day's trek were plotted. If the range (>')(i.e., the smallestarc containing all data in the distribution)was less than or equalto 22.5° (an arbitrarily chosenlimit), the turtle is consideredto have followed a consistentbearingamongdays. Sinceseveralturtles were stationarybetweendays,the first and seconddays of travel do not necessarilycorrespondto the first and seconddays after release. Results Nesting and emergence Fresh E. blandingii nests were protected betweenJune 15 and trailed (m) water (deg.) (r) ("') 84 289 230 240 230 225 0.30 0.90 0.18 0.82 0.89 0.35 280 356 180 317 253 114 180 0 35 . 190 0.38 0.18 -009 0.39 0.76 0.33 0.67 141 191 1994 1a 2b 7a 8b 9c 7 8 5 5 2 7 13a 4.80 -150.00 7.10 14.80 6.20 8.50 6 15.20 1995 1a 2a 6 7a IOC 11a 12C 3 7 1 2 2 9 4 34.95 11.40 10.05 -150.00 11.00 16.01 15.60 172 276 222 289 101 187 228 057 098 273 214 Note: Nestswith a meanvectorlength(r) >0.6 areconsidered to be directed;nestswith r > 0.6 andwhosemeanvectorangle«(II)is within 250of thenearest waterareconsidered to exhibitdirectedness toward thenearest water. aNodirectmovement. bDirected movement; not towardwater. 'Directedmovement towardthenearest water. June 25, 1994, and between June 16 and June 29, 1995. Emergence began on September 6, 1994, and September 13, 1995. Mean incubation time (number of days from oviposition to emergence) was 94.8 days in 1994 and 90.1 days in 1995 H t hI. t. dt tu all fr th ...a c mgs c?n mue 0 emerge na r y om e nest until mId-Octobe~ m both y~ars. The l~test .recorded ~atural emerge~ce for thIS populatIon (excludmg lIve hatchlmgs at excavatIon) occurred on October 25, 1995. Emergence within nests was mostly asynchronous in both years, lasting between 2 and 10 days in 1994 and between 2 and 11 days in 1995. Live hatchlings were uncovered during nest excavations in October of both years. In both years 93.3% of successfully protected nests were that is, they produced at least one live hatchling. Of 103 hatchlings all y (.. I.e., observed d d) f unal e in 1994, th rom e 80.6% emerged nes , .10 natur- 1. t 12 6 07 were a Ive w h en . excavated, a~d 6.8% had successfully hatched but ?Ied before emergmg from the nest. In 1995, of all hatchlIngs observed (n = 119),83.2% emerged naturally, 14.3% were alive when excavated, and 2.5% were dead upon excavation. Hatchlings' body sizes were not significantly different between years (1994: mean CL = 33.1 mm; SD = 1.6 mm; n = 88; 1995: mean CL = 33.5 mm; SD = 1.9 mm; n = 100; 0.0587 < (0.05.(2),186, P = 0.05). Of the six beach nests sampled for hatchling movement in 1994, one faced northeast (azimuth 84°), one due south, and four had a southwest aspect (azimuth 230°,240°,230°, and 225°); the mean distance between beach nests and the @ 1997 NRC Canada - I 1390 Can. J. Zool. Vol. 75, 1997 Fig. 1. Movementof 40 E. blandingii hatchlingsin relationto the nearestwater to the nest in 1994. Each point on the unit circle representsthe angle (v) (azimuthfrom north) of the resultantvector (R) of eachhatchling's first-day trajectory, which has been convertedto the new polar angle (vi) (azimuthin relationto water)so that the direction to the nearestwater is standardizedamong nests.The arrow is the meanvector (m') of the sample;its length (r') is 0.234 and angle (1/>')is 64.70 clockwise from the water. At a significancelevel (a) of 0.05, we acceptthe null hypothesisthat the initial movementis randomwith respectto the nearestwater. WATER t t / n = 40 hatchlings r' = 0.234; <\>' = 64.70 u = 0.893; a = 0.05 vegetatedbeachedgewas2.71 m (SD = 1.87 m; range = 1.0-4.94 m; n = 6), and at emergencethe meandistance betweennests and the nearestwater was 9.43 m (SD = 4.48 m; range = 4.8-15.2 m; n = 6). Of the six beachnests sampledin 1995,threefacedsoutheast(azimuth1010, 187°, and 172°) and three faced southwest(azimuth222°, 228°, and 276°); the meandistancebetweenbeachnestsand the forestedgewas2.88 m (SD = 1.47m; range = 1.7 -5.57 m; n = 6), and at emergencethe meandistancebetweenbeach nestsand the nearestwater was 16.5 m (SD = 9.37 m; range = 11.0- 34.95m; n = 6). The oneroadsidenestsampled in eachyear was approximately7 m from the forested incline and between100and 150 m from the nearestwater. In 1994,42 turtles from sevennestswere powder-marked and trailed for a maximumof 4 days in 1994. Thirty-six hatchlings from sevennestswere powder-markedin 1995 and tracked for a maximumof 11 days. In both 1994and 1995,hatchling orientationon the first day after emergence from the nestwas randomwith respectto the nearestwater (a = 0.05) (Figs. 1 and 2). Nestmatesfrom three nests sampledin 1994 displayed directed movementon the first day (Table 1). In hatchlings from only one nestwas movementconsideredto be directed towardthe nearestwater, althoughneitherhatchlingactually enteredthe water. Hatchlings from two other nestsshowed directedmovementon the first day, but not toward water. In the first case,hatchlingsfrom an inland nestinitially moved down the sloped road shoulder. On the following days, hatchlingsclimbed back up the slopeto cross the road or climbed into the vegetatedincline. In the secondcasehatchlings movedalmostparallelto the water line, a direction that did not follow the topographyor lead toward vegetation. Most hatchlingsfrom this nestwere severelybitten by ants upon emergenceand it is possible that they were moving away from the anthill. Resultswere similar in 1995. For five nests,no directed movementwas shownamongnestmateson the first day of travel (Table 1); however,in two nestsnestmatesdisplayed directedmovementtoward water, although,as in 1994,most hatchlingsthat movedtoward water did not enter it on the first day. Of 27 turtles for which multiday dataare available,only @ 1997 NRC Canada Standinget al. 1391 Fig. 2. Movementof 28 E. blandingii hatchlingsin relation to the nearestwater to the nest in 1995. Each point on the unit circle representsthe angle (v) (azimuth from north) of the resultantvector (R) of eachhatchling's first day trajectory, which has been convertedto the new polar angle (V') (azimuth in relation to water)so that the direction to the nearestwater is standardizedamong nests.The arrow is the mean vector (m') of the sample;its length (r') is 0.168 and angle «f>')is 2.50 clockwise from water. At a significancelevel (a) of 0.05, we acceptthe null hypothesisthat the initial movementis randomwith respectto the nearestwater. WATER t ~ t n = 28 hatchlings r' = 0.168;<1>' = 2.50 u = 1.258;a = 0.05 6 followed a consistentbearingbetweenthe first and second daysof travel(Table2). Of 9 hatchlingsfor whichmore than 2 days of travel are available,only 1 was consistentamong days (4 days; A = 5.8). This hatchling maintaineda route almostparallelto the water line and ultimately its trail was lost at the forest edge. Trail description While the interpretationof trendswithin andamongclutches is important,someof the mostcuriousresultswere revealed throughclose inspectionof individual trails. For instance, not only did mosthatchlingsnot maintaina straightcourse among days, but manytrails within days were convoluted. Hatchlingsfrequentlychangeddirection, looping and backtracking as well as crisscrossingtheir own trail repeatedly. Convolutedtrails were restrictedto openareassuchas the beachand road, althoughnumerousturtles in these areas navigated along fairly straight routes. Interestingly, all hatchlings,regardlessof the characterof their trail in the open, navigatedalong straightcourseswhen under vegetation cover. Numeroushatchlings in this study avoided water. On severaloccasions,hatchlingsfollowed straighttrails in the directionof water, but veeredeither after having reachedit or within a few metres of the shoreline. Frequentlythese hatchlingsresumeda courseinto the woods. In 1994, 6 of 42 trails endedin water or < 10 cm from the water's edge; it is suspectedthat theseturtles enteredwater. Two hatchlings whosetrails werelost> 2 m from waterwere observed at the shoreline aquatic-basking3 days after their initial release.Onehatchlingthatenteredwaterreemergedapproximately6 m westof the point of entry and proceededup the beachtoward the forest. Of 36 turtles tracked in 1995,the trails of 8 endedin water; of these turtles, 1 enteredwater on the first day of travel, walked less than 10 m along the shoreline,and emergedto spendits first night on shore. @ 1997 NRC Canada "., ", 1392 ~ Can. J. Zool. Vol. 75, 1997 Table 2. The rangeas a measureof dispersionof daily orientation (v) of travel routes of individual hatcWings. Range (A) HatcWing Days I and 2 No. of travel Consistentbearing No. of days (A < 22.5°): Over all days of travel of travel (n > 2)* on first 2 days? overilll? IB94 IC94 ID94 1E94 IF94 42.7 61.8 171.8 173.4 2. 7 -.;'"~~ IG94 2A94 2B94 2C94 2D94 2E94 2F94 2G94 2H94 8A94 2A95 2B95 2C95 2D95 2E95 2G95 2H95 6A95 I1A95 11C95 I1D95 IIG95 Total 8.3 99.8 27.4 170.1 163.1 99.6 179.6 93.2 90.0 115.2 1.2 31.8 85.6 1.2 140.5 104.8 110.7 152.3 8.5 4.8 61.4 101.6 --* 78.1 --193.2 -180.4 --5.8 35.6 136.2 --Yes -289.3 233.0 182.4 --Yes ,tt"" :1 '- ~ '"'" Yes Yes ,: 3 3 3 4* 3 4 Yes Yes 6/27 1/9 4* 4 3 -Yes -* Note: If the range is not greaterthan22.5°. the hatchlingis consideredto have followed a consistentbearingamongdays. *The numberof days of travel is not necessarilythe numberof days after release.since someindividuals remainedstationaryfor at least I full day. For example,hatchling 2A95 movedon only 4 of the II days on which it wasobserved. Two hatchlings in 1995 were observed in aquatic overnight forms (sleeping/resting sites) in <3 cm of water. In addition to aquatic forms, hatchlings used overnight and daytime forms similar to those described by Butler and Graham Discussion Many selective advantages of postemergence water-seeking behaviour in hatchling turtles are presumed; these include the (1995), burying themselves in leaf litter and vegetation and nestling in beach cobble, in sphagnum, and under roots and logs. Fossorial movements were observed in both years. Individuals moved from a terrestrial form along a route approximately 10 cm beneath sphagnum and leaf litter. In 1995, several hatchlings spent the night in terrestrial forms, beneath vegetation and leaf litter, or exposed on the beach, when temperatures fell below freezing (-5.5°C). Generally, hatchlings showed no propensity for seeking cover or for following slope. Infrequently, trails overlapped, but only for short distances « 2 m). Nestmates released on the same day showed no tendency to move in the same direction as one another on the first day or subsequentdays. Trails shown in Fig. 3 are representative of patterns observed in all nests sampled in this study, though none of these hatchlings followed a tortuous trail in the open; all were released on the same afternoon. avoidance of avian and terrestrial predators, access to suitable basking and feeding habitat, and decreased risk of thermal stress and desiccation. However, few supporting data are available. For freshwater turtles at high latitudes, water should be particularly important if hatchlings emerge from the nest in autumn because it provides insulation against tissue freezing during winter. Throughout the range of E. blandingii, hatchlings emerge from the nest in autumn (Butler and Graham 1995; Ernst and Barbour 1989; Power 1989; Congdon et al. 1983; Bleakney 1963); it is generally assumed that neonates seek aquatic hibernacula. However, females typically nest inland (Butler and Graham 1995; Ross and Anderson 1990; Petokas 1986; Congdon et al. 1983), where the view of water from the nest site is often obscured by vegetation. Although few detailed descriptions of nesting sites exist for this species (Butler and Graham 1995; Power 1989; Petokas 1986), it appears that @ 1997NRC Canada ; Standinget a/. Fig. on avoidance. among ', 3. the Early same days; 1393 POstemergence day. These they trails They patterns did showed not of no Were orient 8 E blafldingii propensity observed themselves to in mOst with hatchlings Scent-trail respect nests in one in another to this vegetation, study. a Nova SCotia nor water, Population. to follow or any slope other Nestmates Or a Were Consistent beach feature, :iiiiiiiiiiiiiiiiiiiiiiiiiiiiii released compass and at bearing there is evidence .Nest 0 CJ]Tree OVernight [onn COVer Water 5m ::::::::::::::::::::::; --:::::::::::::::::::; the nearestWaterbody to inland nestsis often marshor WetEhrenfeld 1968; Ehrenfeldand Carr 1967; Anderson1958) land and not a large bOdyof openWater(Butler and Graham upon emergence,since thesecues Would be ineffective in 1995; Power 1989; Petokas1986; Congdonet al. 1983).It orienting from inland nests. is unlikely, then, that orientation mechanismssimilar to Our findings suPPOrt thoseof Butler and Graham(1995), thoseof neonatemarineturtlesand beach-nesting freshwater who concludedthat slope,openhorizon, and the silhouette turtleshaveevolvedin E. blandingii. That is, it is unreasonof nearbyvegetationdo not appearto be critical cuesin the able to assumethatE. blandingiihatchlingsusecuessuchas orientationof E. blandingii hatchlings(Figs. 1, 2, and 3, slope,photic gradients,openhorizon,and vegetationsilhouTable 2). Although Butler and Graham (1995) provided ette (Lohmannand Lohmann 1996; Godfrey and Barreto limited evidenceof an olfactory componentin orientation, 1995;Salmonet al. 1992; Witheringtonand Bjorndal1991; that simUltaneouslyreleasednestmatestended to disperse @ 1997 NRC Canada the nest site within or of Water 1394 ICan. randomly fixate (Table 2, Fig. on an olfactory structural visual feature. cues while (personal the orientation open, migration vegetation possibility mechanism ment efficiency investigation. Regardless of the actual movement random with respect wandering is adaptive, newly emerged able to find water with "seek" water, a way that they Although finding to water" our results their conclusion in their own conclusion. and For of tracked "necessarily water" standing .in order Butler are also water," the from used Graham 1995). In our study, ...ery hat~hlmgs dIsplayed respect to water entere? water, McNe~1 (1996, hatchlmgs dry (FIgS. others pool 1 and 2); overtly see footnote released vernal for (Butler several and wIth turtles 3). Data that newly s edge are repelled from emerged vanation of e~ergent to dIsperse ~atchlmgs, m both as well as t~e tendency the Nova.ScotIa in distribution from et al. Understanding in and spring of this part and presents because in part interesting man- of its small because of its behavioural populations elsewhere 1995; Power et al. hatchling may be another population. behaviour size and in the species' range 1994; Power 1989). in this threatened popu1a- tion is a conservation priority. It is hoped that the protection of younger age-classes, particularly hatchlings, will bolster recruitment vival into the adult population. and associated E. blandingii Scotia through this habitat is important Scotia. terrestrial overwintering greater detail because survivorship, habitat of in Nova surrounding Not only do hatchlings nesting need to move in search of hi berna cuI a, but the integrity may affect the efficiency identify of nestto the sur- Additionally, to hatchling that future work on this of their travel. population sites used by hatchlings, the behaviour of young our understanding conservation The protection waterways in Nova importance and elsewhere, Scotia to and study age-classes. of the species needs of the Nova We attempt This in will and the particular population. Acknowledgements We gratefully World of an~ Mas~a- acknowledge Wildlife Fund Fund; Acadia 24.55 Fund; Nova Department Program; support by water. Our results i~ply not o.nly that wa~er may not be the go.al but als~ t~at no sImple habItat fe~ture IS sought. The behavioural nestmates hatch- terrestrial be accomplished emergence of E. blandingii problems, improve the and dis- and. whI!e It (FIg. population patchy of withstanding hatchlings movement 4),suggest at the water with course rando?I avoIded strategy recommend in ~abitat, habItat Delayed This has not been blandingii since ice scouring and November. standing "repeat- a straight pool Scotia, facet of the bet-hedging agement but this if E. destroy overwintering nests. Nevertheless, are uncovered in Nova Scotia nests in late of the vegetation some of the of flooding would live hatchlings Vol. 75, 1997 that this could in Nova they fail habitat] majority vernal proportIonately (1995) hatchlings [wetland it is unlikely the nest cavity October nest, Even capable areas must be protected. not in concordance deviated to encounter in such 'seek In fact, are physiologically its potential as possible. and Graham's although sought be in the in the literature. ing habitat if neonates open horizon, the nest. instance, non-randomly absence be organized as directly that hatchlings' report should should toward from behaviour Thus, goal or the so as to avoid E. blandingii lings divergence (Herman selection to have to organize their efficiency. support upon emergence results edly their further mechanism, If water-seeking movements reach the move- warrants natural animals neonate of a lack of orientation support this their The environment relative that in the orientation 1991). suggests impaired hatchlings to their (Able is more cover and influences overwintering hibernation, its effectiveness. structure cues, one would expect mechanisms that allow use was also noted This hatchlings substantiated do not seek or is not totally of E. blandingii primarily individuals vegetation may improve not the nest. Such behaviour that the vegetation relevant favoured from communication). cover do on a particular that hatchlings in the open. Butler than the movement of when they are under convoluted by B.O. initial that hatchlings more that hatchlings our data suggest avoid vegetation, directed (straight) more any We postulate in their Although 3) implies cue J. Zool. the ford, Canada. S. individuals following: T. Recov- Canada for Species E. Whidden, Muntz, and data. assistance R. D. T-shirt also supplied historical their Article Scotia Nicholas, Whynot. logistic We thank in gathering E. Alcorn, R. Charlton, C. P. Hope, R. MacFarlane, J. McNeil, Mockford, Turliuk, the Species Endangered Parks and access to unpublished following from University Faculty Association Scotia Liquor Commission/Nova of the Environment Parks field data: T. Gilbertson, T. funding Canada-Endangered Drysdale, L. MockT. We Ramey, also thank chusetts populatIons, ~uggest that .hatchl~ngs .of .thiS specIes may have a bet-hedgmg or adaptIve com-fllppmg strategy S. Bondrup-Nielsen, J .S. Boates, P. Taylor, O. Kukal, and the anonymous reviewers for their suggestions and criticism upon emergence. (Cooper a~d Kaplan 1982; Cooper In an unpredIctable e~vIro~ent such as Nova of the manuscript; D. Ryan for his statistical design and analysis; and B.O. Butler and G. where the onset and seventy hatchling October, emergence a mixed of wmter is delayed strategy would vary until among 198~). ScotIa, years and mid-September ensure their insight expertise Packard in for and communications. and that some offspring References survive. (1996, seeThat footenote numerous 4) studies hatchlings survived in overnight our and atMcNeil's temper- Abl~, K.P. 1991. Common themes and VarIations m arumal onenta- atures limited tlon systems. Am. Zool. 31: !57-l67. 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