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Observations of Spencer's 'Skink Pseudemoia spenceri' from within the high canopy of an overmature Mountain Ash 'Eucalyptus regnans' PDF

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Preview Observations of Spencer's 'Skink Pseudemoia spenceri' from within the high canopy of an overmature Mountain Ash 'Eucalyptus regnans'

Contributions Observations ofSpencer’s SkinkPseudemoia spenceri from within the high canopy ofan overmature Mountain Ash Eucalyptus regnans M Grant Harris1 Brett Mifsud2 and Graeme RGillespie3 J , 'SchoolofLifeandEnvironmentalSciences,DeakinUniversity,221BurwoodHighway,BurwoodVictoria3125 27ColstonAvenue,Sherbrooke,Victoria3789 3FloraandFaunaDivision,DepartmentofLandResourceManagement,VanderlinDrive, Berrimah,NT0828 Abstract DuringMarch2012,whilstundertakinganaerialsurveyofanovermatureMountainAshEucalyptusregnans inToolangiStateForest,aSpencersSkinkPseudemoiaspenceriwasobservedinthecanopyataheightof-50m abovegroundlevel.Inthefollowingyear,whilstsurveyinganotherovermatureE. regnans,apairofP.spenceri wasdetectedatsimilarheightwithinthecanopy.ThesesightingsdemonstratethatthermoregulationinP.spen- ceriisnotrestrictedtodeadtreesandthathighcanopiesofovermaturetreesmaybeanimportantcomponent ofitshabitat.Duetothedifficultyofaccessingtheforestcanopyitislikelythatourunderstandingofarboreal habitatusehasbeenunderestimatedforsmallvertebratessuchasskinks.Ourserendipitoussightingsempha- sisetheneedforfurtherresearchinthisarea. (TheVictorianNaturalist131(I)2014,24-27) Keywords: Spencers Skink Pseudemoia spenceri, Mountain Ash Eucalyptus regnans arboreal, , canopy Introduction ObservationsofSpencer’sSkink Spencers Skink Pseudemoia spenceri is an in- In March 2012, as part ofan ongoing project sectivorous species found in wet sclerophyll to document Victorias largest trees (Mifsud forest (Rawlinson 1974) and montane dry 2003), a Mountain Ash Eucalyptus regnans 73 woodland (Clemann 2002). With well devel- minheightand245.5m3trunkvolume(Mifsud oped five-toed (pentadactyl) limbs, dorso- 2012unpubl. data)wasclimbedwiththeuseof ventralflatteningand high agility, R spenceri is arboriculturalmethods(DialandCarl 1994) in the most arboreally adapted of south-eastern Toolangistateforest (37° 33'59S 11"S, 145°27' Australian scincids (Brown 1986). The use of 47.43" E). The treewas overmaturewith abro- aerial tree microhabitats provides opportuni- ken top, which is characteristic ofthis growth tiesforbasking(Webb 1985;BrownandNelson stage (Ashton 1975). Using records of stand 1993), foraging(Brown 1986),shelter (Rawlin- replacing fires in the area as a dating method son 1974;GibbonsandLindenmayer2002) and (Ashton 2000), the tree was estimated to be predator avoidance. Previous records of the -400years ofage. The tree waslocated within vertical extentoflivetree usebyP.spenceriare an area ofwet sclerophyll forest characterised 10 m (Pengilley 1972 cited in Webb 1985), 22 byanoverstoreyofE. regnans,amidstoreytree m (BrownandNelson 1993)and 15m (Homan layer ofBlackwood Acacia melanoxylon, Silver 2011) above ground level. Rawlinson (1974) WattleAcaciadealbata, Myrtle Beech Nothofa- documentedtheuseofaerialmicrohabitats50- gus cunninghamii and a tall shrub layer ofSoft 75mabovegroundlevelbutbelievedPspenceri Tree-fernDicksoniaantarctica RoughTree-fern , to be restricted to dead trees andprimarily as- CyatheaaustralisandMuskDaisy-bushOlearia sociatedwithpost-firestandsinwetsclerophyll argophylla(Costermans 1983). Duringthissur- forest. The validity of Rawlinsons report was vey, askinkwas observedwithin thecanopyat m questioned (Webb 1985) andasadditional ob- aheightof-50 abovegroundlevel.Thisindi- servationsofP. spenceriat this heighthave not vidual did not exhibit an evasive response and been documented it remained unclearto what activelyclimbed onto the legs andbodyofthe extentthisandotherspeciesmay usetheforest surveyor (Fig. 1). On 23 March 2013, during canopyintemperatesouth-easternAustralia. the survey of another overmature E. regnans, 24 TheVictorianNaturalist Contributions Fig. 1.SpencersSkinkontheleg-strapofasurveyorsharness.PhotobyMikeHanuschik. m m 65 in heightand 170 3 trunkvolume (Mif- Discussion sud 2013 unpubl. data) and also in Toolangi Rseudemoia spenceriforages on theforestfloor State Forest, a pairofP. spenceri was observed and in aerial tree habitats with detritivorous ataheightof50mabovegroundlevel. One in- insects such as saprophagous flies (Diptera), dividualwasbaskingin asunspotonthetrunk cockroaches(Blattodea)andtermites(Isoptera) (height 55 m) and the other was stationaryon formingasignificantcomponent(40.7%within a dead limb below thefirst. Neither individual sample, n=82) ofits diet (Brown 1986). Obser- m exhibitedanevasiveresponse orchanged posi- vations of ground based habitat use (<1.2 tionsasweascendedadjacenttotheirlocations. above ground level) recorded logs as the most Theindividualthathadbeenbaskingproceeded commonly occupied substrate (78% ofobser- to climb onto the bodyofa surveyor, remain- vations) withthemajority(96%) ofthese being ing mainly stationary with periodic shuttling partlydecayed(Webb 1985). Assubstrateuseis betweenthesurveyorsarm,shoulderandback oftenassociated with preycaptureitcan bein- foraperiod of15 minutesbefore beingcoaxed ferred that decaying coarse wood mayprovide to return to the tree trunk (Fig. 2and 3). With important foraging opportunities at ground the exception of the aforementioned encour- level; however, gut content analysis by Brown agementtoleave thesurveyors body there was (1986) indicates thatarboreal invertebrateprey nohandlingorintentional interaction with the obtained from aerial tree foraging also form a animals. A dark brown-olive colouration with majorproportion (52.3%within sample, n=82) golden-cream dorsolateral stripes, which are ofthedietofP.spenceri. Goldingayetal(1996) diagnosticcharacteristicsofP.spenceri(Cogger noted a greater abundance ofP spenceri with 2000; Wilson and Swan 2010) were present in an increase in log density following timber theobservedanimals. harvestingand an absence ofP. spenceri in un- Vol 131 (1) 2014 25 Contributions Fig.2.SpencersSkinkonthearmofasurveyor.PhotobyDamienNavaud. loggeddryforestplots.Thissuggeststhatdead- allow it to function as a photosynthetic organ wood with environmental moisture conditions (Sillettetal. 2010). Thesightings reported here conducive to the establishment of wood de- ofP. spenceribaskingonthesmooth E. regnans cay and associated saprophagous invertebrate barksupportsthe proposition that foran agile communities could be a critical resource for heliothermsuchasP.spenceri,thelevelofinso- P spenceri. In addition to the quantityofdead lation received on a live overmatureE. regnans organicmaterial (logs and litter) thelevel ofin- stem is likely to be sufficient for basking and solation is an important influence on patterns suggeststhatthermoregulation isnotrestricted of habitat usage in skinks within sclerophyll todead trees. forests(Kutt 1999). Both elevationabovetheunderstoreyandthe Climbing emergent trees to rise above un- presence ofaerialdeadwoodare defining char- derstoreyvegetationandtherebygain accessto acteristics of overmature E. regnans (Ashton direct sunlight forthermoregulation, may be a 1975; Mifsud 2003), and ourobservations sug- driver ofarboreal behaviour (Rawlinson 1975; gest that these trees may provide an important Webb 1985;Kutt 1999). Thishypothesisissup- combination of resources for P spenceri. The ported by the findings of Brown and Nelson availabilityoftheseresources(aerial deadwood (1993), who noted the absence of P. spenceri andelevationforinsolation) provided byliving at ground level in the successional stages of E. regnansarelikelytoremainlongerthanpost- wet sclerophyll forest with the densest canopy firestagswhich aremoredisposedtostructural cover (11-63 years old). At the scale ofan in- collapse (Gibbons and Lindenmayer 2002), dividual overmatureE. regnans theisobilateral thus allowing P. spenceri populations to use leafshapeallowshighlevelsoflightpenetration oldgrowth forest. This hypothesisissupported throughthecanopy(Keithetal.2009),allowing by the findings ofKutt (1999) who recorded a insolation ofthe trunk. It has been suggested significantly greater abundance of P. spenceri thatsufficientlightreachesthe smooth bark to in mature growth compared to 25-35 year old 26 TheVictorianNaturalist Contributions andFrost, 1894) (Lacertilia:Scincidae) aspeciesendemic to south-eastern Australia. The Victorian Naturalist 103, 48-55. BrownGWandNelson JL(1993) Influenceofsuccessional stageofEucalyptusregnans(mountainash)onhabitatuse by reptiles in the central highlands, Victoria. Australian JournalofEcology18,405-417. ClemannN(2002)Aherpetofaunasurveyofthe Victorian Alpineregion,withareviewofthreatstothesespecies.The VictorianNaturalist119,48-58. CoggerH(2000)ReptilesandamphibiansofAustralia.6edn. (ReedBooks:ChatswoodNSW) CostermansL(1983)NativetreesandshrubsofSouthEastern Victoria.(WeldonPublishing:Melbourne) Dial R and Carl TS (1994) Description ofarborist meth- odsforforest canopyaccessandmovement.Selbyana 15, 24-37. GoldingayR,DalyG andI>emckeri F (1996) Assessingthe impactsofloggingon reptilesandfrogs in the Montane Forests ofSouthern New' South Wales. Wildlife Research Gi2b3b,o4n9s5-P5a1n0d.LindenmayerD(2002)Treeholmlowsand,wil..d.- lifeconservationinAustralia.(CS1ROPublishing:Colling- wood) Homan P (2011) A record ofSpencer’s Skink Pseudemoia spencerifromtheVictorianVolcanic Plain. The Victorian Naturalist128,106-110. Keith H,MackeyBGandLindenmayerDB(2009)Re-eval- uationofforestbiomass carbon stocks and lessons from the worldsmost carbon-dense forests. Proceedings ofthe NationalAcademyofSciences106,11635-11640. KuttA (1999) Initial observationsoftheeffectsofthinning EucalyptregrowthonHeliothermicSkinksinlowlandfor- desitv,erEsaestdiGsciippplsinlea,npdpV.i1c8t7o-r1i9a6.InEHdesrDpetLoulnongeyyinanAudstDraAlyiear:sa. (SurreyBeatty&Sons:ChippingNorton,NSW) Fig.3.SpencersSkinkonthearmofasurveyor.Pho- MifsudBM(2003)Victoria’stallesttrees.AustralianForestry tobyDamienNavaud. 66,197-205. Pengilley R (1972) Systematic relationships and ecology of regrowth stands. Documenting the use ofliv- spuobmleis(hyegdosoPmhiDneltihezsairsd,sfAruosmtrsaoluitahneaNstaetrinonAaulstrUanliivae.rs(iUtny-) ingovermaturetreesbyR spenceri isimportant citedinWebbGA(1985)Habitatuseandactivitypatterns to the management ofthis species in relation iAnusstoramleiasnofurtohgesaastnedrnrepAtuilsetsr,aplpi.a2n3-s3k0i.nkEs.dIGnGVriieggb,ioRloSghyinoef to forestry practices as retention ofindividual and H Ehmann (RoyalZoologicalSocietyol NewSouth overmatureE. regnansmayhavesignificant in- RaWwallienss:oSnydPnSey()1.974) Revisionoftheendemicsoutheastern fluence on their distribution. Whilst not listed Australian lizard genus Pseudemoia (Scincidae: Lygo- asathreatenedspecies,thesefindingsalsopro- sominae).MemoirsoftheNationalMuseumofVictoria35, 87-96. videfurtherevidenceoftheimportanceofold- SillettSC,Van Pelt R.Koch GW,AmbroseAR,CarrollAL, growthforestformaintainingforestfauna. AntoineMEandMifsudBM(2010)Increasingwoodpro- duction through old age in tall trees. Forest Ecology and Acknowledgments Management259,976-994. Thankyou to Julia Chilcott, Mike Hanuschik, Ewan WesboubthGeAast(e1r9n85A)usHtarbailtiaatnusskeinaksn.dIanctTivhietybipoaltotgeyrnosfAinusstroamle- cMounrtrraiyb,utDiangmioeutnstNaanvdaiungdtarneedcIlnigmrbiidngO,opshtoerthougirsapfhoyr iHanEfhrmogasnann(dRoryepatlilZeso,olpopg.i2c3a-l30S.ocEidetGyoGfrNieggw,SRouSthhinWealaensd: andproof-readingskills. Sydney). WilsonSandSwanG(2010)Acompleteguidetoreptilesof References Australia.3edn(NewHollandPublishing:Sydney) AshtonDH (1975)TherootandshootdevelopmentolEu- calyptusregnansF.Muell.AustralianJournalofBotany23, 867-87. AshtonDH(2000)Theenvironmentandplantecologyofthe HumeRange,centralVictoria.ProceedingsoftheRoyalSo- BrcoiewtnyoGfWVict(o1r9i8a6)11T2,he18d5i-e2t7o8f.Pseudemoiaspenceri (Lucas Received30May2013;accepted8August2013 Vol 131 (1)2014 27

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