ResearchReports Gone but not forgotten: The status ofthe Stuttering Frog Mixophyes balbus in Victoria Graeme RGillespie1 KwaiChang Kum2 David A De Angelis3and Bradley D Jenner3 , , 'FloraandFaunaDivision,DepartmentofLandResourceManagement, CSIROComplex,564VanderlinDrive,Berrimah,NorthernTerritory0838 2ZoosVictoria,RO.Box74,Parkville,Victoria3052 5EarlyPlace,Boronia,Victoria3155 Abstract TheStuttering Frog, Mixophyesbalbus,isathreatenedspeciesrestrictingtouplandstreamsincoastaldrain- agesofsoutheasternAustralia.There havebeennoconfirmedsightingsotthisspeciesinVictoriasince 1983 and it has suffered marked declines throughout its range. We undertook surveys targeting suitable habitat throughoutthepotentialVictorianextentofrangeofthespecies,inordertodetectanyremainingpopulations andascertainitscurrentconservationstatus.Nineteen stream reacheson 12differentstreamsweiesampled withatotalof41.7kmofwatercoursesearched. NoStutteringfrogsweredetected,but allotherfrogspecies expectedtobeassociatedwithstreamsintheareawerefrequentlydetected.Thesefindingsbuildonprevious evidencethattheStutteringFroghasdeclinedthroughoutitsrange,andmayinfactnowbeextinctinthewild inVictoria. (TheVictorianNaturalist,131(3),2014,64-71) Keywords: amphibian declines; extinction;chytridfungus;conservation assessment Introduction Amphibian population declines, both in Aus- ers alongthe eastern fall ofthe Great Dividing tralia and worldwide, have received much at- Range from north-eastern New South Wales tention over the past 25 years (Stuart et al to the Gann River catchment in eastern Victo- 2004). Within Australia, since the late 1970s ria (Gillespie and Hines 1999). Historically M. at least threespecies mayhave become extinct balbus was widespread in central and north- NSW andafurther37 specieshaveundergonepopu- ern and considered secure (Gillespie lationdeclinesandrangecontractionswarrant- and Hines 1999). Duringthe 1980s and 1990s, ingRedlistingbythe IUCN (Hero etal 2006). the species underwent a noticeable decline Many of these declines have occurred within across much ofits distribution (Mahony 1993; protectedareas orinotherareas whereanthro- GillespieandHines 1999). Althoughtherewere pogenic disturbances havebeen minimal (Stu- fewerhistoricrecordssouthofSydneyandonly artetal2004). three from Victoria (Gillespie and Hines 1999; In the late 1990s a novel pathogen, the am- NSWWildlifeAtlas),thespecieshasnowdisap- phibian chytrid fungus Batrachochytrium den- pearedfrom nearlyallknownhistoricalsitesin drobatidis (Bd), was discovered (Berger et al thoseregions(Lemckertetal 1997; Daly 1998; 1998), and has since been implicated as a ma- Gillespie and Hines 1999; Daly et al 2000). jor cause of amphibian declines, particularly Targeted surveys have detected the species at for so-called enigmatic declines in minimally onlythreelocalitiesinNSWsouthofSydneyin disturbedareas (e.g.Lipsetal 2006). However, thepast 10years (Dalyetal 2000;White2000; habitat loss and alteration, along with other Hunter2001; Hunterunpublisheddata). threatening processes, such as invasive species Mixophyes balbuswas lastseen in Victoria in and pollution, have played important roles in 1983 (GillespieandHines 1999).Generalfauna the declines of many species (Gillespie et al surveys in EastGippsland conductedsince the 2011).Morerecently,evidenceismountingthat 1980s did not locate this species (see Lugg et climate change isalsoadverselyaffecting some al 1993); however, there was relatively lim- speciesandcommunities(Laurance2008;Bick- ited survey effort targeting cryptic amphibian fordetal2010). species such as M. balbus (G. Gillespie pers. The Stuttering Frog (or Southern Barred obs.). Additional, more targeted surveys since Frog) Mixophyes balbus (Fig. 1) occurs in riv- the mid-1990s have also failed to locate any 64 TheVictorian Naturalist ) ResearchP,eports Fig.l. TheStutteringFrog Mixophyesbalbus. Photo: GGillespie individuals (Holloway and Osborne 1996; G. EastGippslandinanattempttofindanyextant Gillespieunpubl. data). populationsofM. balbusinVictoria,andtore- Mixophyes balbus is currently listed nation- assessitsstatus. allyasVulnerable (EnvironmentProtection and Methods Biodiversity ConservationAct(EPBC 1999). In The survey focused on the greater catchments VtiacxtoonribayMt.hebaVlibcutsoriisarnegFilsotreareadnadsFaatuhnraeaGtueanre-d of the Cann and Genoa Rivers, because M. antee Act 1988 (FFG), and listed as Critically balbus is historically known from these catch- EVenrdtaenbgraetreedFaounntaheinAdvViisctoorryiaLis(tDoSfETh2r0e1a3t)e.neAd malesnotss,abmoptlhediniVnictthoeriBaeanmdmNSRiWv.erOncaetcsihtmeewnats, NationalRecoveryPlanforM. balbushasbeen westoftheCann River. Samplingsiteswerese- published (HunterandGillespie2011),andthe lected from satellite imagery and topographic Department ofEnvironment and Primary In- maps. Sites that werelikelyto meet the follow- dustries (DEPI) has drafted a Flora and Fauna ingcriteriawerechosen: Guarantee Action Statement for this species •Streamstypicallyperennial; (DSE2009). • Welldevelopedriparianwetforestorrainforest; Knowledge ofthe former distribution ofM. • Steep-sidedbanks ratherthanwideterraces; balbusinVictoriaisverylimitedsincetherewas • Streambedswiderthan 1 m; minimal survey effort for riverine frogs in the • Streamswithgravel/stonyorrockysubstrates; region before the recognition ofdecline. Fur- • Up-stream ofroadcrossings. thermore,thespeciesishighlycryptic,andmay Thefirstfourcriteriareflectthetypicalfeatures remain undetected at low population densities ofmanyofthesitesatwhichM. balbuspersists inpoorlysurveyed areas. Newinformation ac- in NSW. The last criterion favours sites that quired in recentyearson surveytechniquesfor have relatively low historic disturbance levels. rare stream-breeding frogs suggests that previ- Two historic sites were also re-sampled; Ten- o(eu.sg.sGaimllpelsipnigeaefnfdorHtolmlaisy1h9a9v6e;Gbielelnespiinead1e9q9u9;atDe nEaysstonBrCarnecehk)annedarFltahteRNocSkWCrbeoredker(.CaTnhneRtihvierrd Hunterunpubl.data). Inparticular,insufficient historic site, Jones Creek, was not investigated lengthsofstream were surveyed andtherewas becauseadvicefromDavidCameron(Botanist, alackofsurveyfocusonlarvae.Consequently, Arthur Rylah Institute, DEPI) suggested that, manypartsofthe species’ southern range may asa resultofthe 1983 fire andsubsequentero- not have been adequately sampled. We under- sion, this catchmenthas undergone significant tooktargeted surveysofselectedcatchments in geophysical,hydrological andfloristicchanges, Vol 131 (3) 2014 65 Research Reports suchthatM. balbusisunlikelytopersistthere. A minimum of1 km was searched by dayand Surveyswereundertakenbetween 19Novem- bynightateachsite.Forallsurveyshygienepro- ber2011 and23January2013.Allsamplingwas tocols (NPWS 2000)werestrictlyadhered toin undertakeninthemonths ofSeptembertoJan- ordertominimisetheriskofspreadingBd. uary. Eachstream was searched duringthe day Results bytwoormorepeoplewalkingslowlyupstream Atotal of41.7kmofwatercoursewassurveyed in the watercourse searching for tadpoles and egg nests. Flat-bottomed dip nets (bag >35 cm across19streamreacheson12differentstreams wideX<60cmdeep, meshsize0.9-4mm)were (Fig. 2; Table 1). Mixophyes balbuswas notlo- cated at any sites sampled. All other stream- periodically swept over the substrate in pools breeding species known from East Gippsland aobnsderqvueirestefrorsaepctpiroonxsimoafterlifyfl1estoby2 moinneuteosr.tAwlol w(Leirteorilaoccaitterdopaa,loL.nglemsuoesutri,starnedamLs..nuCdriidniigaitsuisg-) tadpoles detected were captured by dipnet and identified (see Hero and Gillespie 1993; Anstis nifera, Litoria citropa and L. nudidigitus were abundantatmostsitesandshowednoevidence 2002). Eggnestsweretargeted sinceMixophyes ofpopulationdeclinessinceobservationsmade balbusmaybreedat thistimeoftheyear. in the 1980s and early 1990s by one ofthe au- Streams were searched for frogs at night by thors (GG).Litorialesueuriwaslesscommonat two or more people walking slowly upstream. the sitessampled;however, thisspecies prefers Mixophyes balbus hasa conspicuous eye-shine moreopenforesthabitatsonwiderwatercours- readilydetected withahead torch. Areas both es in eastern Victoria (Gillespie 2002), and within thestream marginsandalongbanks up m was not expected to be common in the habi- to 10 from the watercourse were searched. Callplaybackwasnotused asthiswasnotcon- tatstargeted forM. balbus. Fiveotherlentic,or facultative stream-breeding, species were also sideredareliablesurveymethodforthisspecies; located:Limnodynastesperonii Litoriaaurea L. however, frog calls were monitored and noted. , , All frogslocatedwereinspectedand identified. ewingii,L.peronii,andL. verreauxii(Table 1). . Research Reports Limnodynastes peronii signifera Critiia verreauxii Litoria peronii Litoria ewingii Litoria nudidigitus Litoria Litorialesueuri Litoriacitropa Litoria aurea of Numberobservers (Km) Distancesampled 05/12/2010 Date M <-Nl u Site u M^rgSCC<rOU-'=*-"NNtC£oO^^On -uJC^UO3UnLNbTNo^of-IrH£oO*O*N CrUD_CcOnh=*((^cfNoNKNOo'OON ^UC-6L,1r»o—ON ^Sg2u23TCga3o«^Nomionn ^^nD|5w=Nror•^’o"'ooto—on U4co^Cb2.=NcC<o"oONoomoCertnN* SandyCWaterkholes234’750°";4137469”° Vol 131 (3) 2014 67 < • ResearchReports <S3 § « I 2 •S ’£ •S cV£> X •2 * sv. i ^ I a:s if a bo IS ^ •ts .2 3 •2 2 If •§ * 1 2 •^~ aa o Jr-2n) >•_ £ O CL. x% «S Q <® o CJ M M I UCQ=or•o"bi—oon OJ<<-uuf -O<^°—an« ^0o,C«335QJ Tr,o--oi. u3Mtg®<rh/-D>S-rroO-!1<'<.( "x—MC3-)3Q•z<irtc u_^u«u1CJJ;=Oo(m.N„-=0^mo0 PrUc«V-§*-<,=mtV-'\O"=^TO2NfNO M•—73a^O^,j^<Nro,—No„°vO\»oK—oNf r22C«zQ3ro——oQ«O-Oo-nH M0TCwCM3r23QJZ=.rO—LoroOO"•O-^O0Orot-NN0<H 68 TheVictorianNaturalist Research Reports Discussion Victoria,TennysonCreekandFlatRockCreek, Thepresentsurveybuildsonpreviousattempts oradjacenttributarieswithsimilarhabitat.The tolocateAT. balbusin Victoria. Thespecieshas Flat RockCreeksiteappearstohaveundergone notbeen seen in Victoria for30 years, and has significant habitat changes since the original not been found in NSW south ofEden since report, possibly from disturbance associated the early 1990s (Hunter and Gillespie in re- with improvements to and usage of the ad- view). Urlus and Marr (2011) reported a call jacent Cann Valley Highway. It seems highly record ofAT. balbus from the Thurra River in likelythatM. balbusisextinctatthesesites.The March2011;however,thisrecordisconsidered intense 1983 forest fire that burnt through the unreliable and highly doubtful (Clemann and Jones Creek warm temperate rainforest refer- Gillespie 2012). Without doubt, the species ence area, followed by extensive erosion and has undergone a severe decline throughout subsequent forest regeneration (D. Cameron the southern part ofits range in Victoria and pers. com.), have almost certainly rendered southern NSW. this historic site unsuitable for M. balbus, due Availableevidencesuggeststhatthemostlike- tosedimententrainmentofthe streambed and ly cause ofdecline ofAT. balbus is Bd. The de- drastically reducedwaterflows. Henceitseems clinecoincideswith thatofmanyotherstream- highly probable that the species is also extinct breeding species in Australia (e.g. Berger et in JonesCreek. al. 1998; Gillespie and Hines 1999), for which The pattern of the historic records strongly Bd has also been implicated. Bd is present in suggests that M. balbus was more widespread temperate stream systems in eastern Victoria than recent information suggest. The three and southern NSW (Kriger et al. 2006). Other historic sites have notably different habitats: potential causesofdecline, such as habitat loss Flat RockCreek - DryForest, Tennyson Creek and alteration (Gillespieetal.2011) orinvasive - Riparian Forest (through Dry and Damp fish species (Gillespie and Hero 1999) can be Forests); and Jones Creek - Warm Temperate discounted. Much ofthe habitat of M. balbus Rainforest. Reports in theliteratureofthespe- within Victoria remains reasonably intact and cies being associated principally with rainfor- mostofthecatchmentareasinwhichAT. balbus estandwetforest (e.g. Daly 1998; Anstis 2002) potentially occurs are free of introduced fish undoubtedly reflect observations of the spe- predators, such as trout. However, nothing is cies innorthern partsofits range whereitwas knownabout thepotential impactoffoxesand historically most frequently encountered (see cats on frog populations, and large terrestrial Gillespie and Hines 1999). Temperature and frogs may be quite vulnerable to predation by suitable breeding habitatare typicallythemost thesespecies (Gillespieand Hines 1999). important factors influencing stream-breeding Climatic factors may also be involved in the frog species distribution (Duellman and Trueb decline ofAT. balbus, and mayworkin concert 1994). Climatic and biogeographical factors with Bd (sec Pounds et al. 2006). However, in may have limited M. balbus to the east ofthe theeventthatclimatechangeleadstoincreased Bemm River catchment, but its historic eleva- NSW stream water temperatures, reduced winter tion range inVictoria and southern (ap- stream flowsand reducedenvironmental suita- proximately 100-1000m)suggeststhatitoccu- bilityforBd,itmayinfactfavoursomestream- piedalargethermalgradient. Suitablebreeding breeding amphibians at the southern limits of habitatforAlbalbus,comprisingpredominant- theirsubtropical/warm-temperateranges. lyperennialstreams, with shallowgravel/Stony Is AT. balbus extinct in Victoria? All historic shoalsforeggnests,andlenticpoolsfortadpole recordswere made incidentallyand apparently development, occurs within these catchments, with relative ease (M Littlejohn pers. comm.; and most ofthestreams we sampled had habi- Museum Victoria records), possibly reflecting tat characteristicsthatappearedhighlysuitable relatively higher historical population densi- forthespecies.Therefore,historicallyAT. balbus ties. Subsequent repeated searches (Holloway mayalso havebeen morewidespreadthrough- and Osborne 1996;G Gillespiepers. obs.)have out the tributaries of these catchments than failed to locate the species at historic sites in currentdataindicate. Vol 131 (3) 2014 69 , : Research Reports Holloway and Osborne (1996) undertook Victoria. However, with the exception of L. a survey of stream-breeding frogs across the aurea, there have been no adequate targeted potential Victorian range ofM. balbus but did surveys or ecological studies ofthem to prop- notlocate thespecies. Atthattime, knowledge erlyassesstheirdistributions,populationstatus ofsurvey techniques for rare stream-breeding and ecological requirements. Hence the im- frogs generally, and M. balbus specifically, was pacts ofvarious potentially threatening proc- verylimited.Wenowknowthattadpolesearch- esses, and the adequacy of current conserva- es need tobean integralcomponent ofM. bal- tion measures orprotected managementareas, bussurveys,asthisisthemostconspicuous life cannotpresentlybeassessed. stage ofthe species. Due to the potential low Acknowledgements abundance and highly patchy distribution of This work wasjointly funded by theDepartmentof thisspeciesalongwatercourses, samplingeffort Environment and Primary Industries andZoos Vic- along stream reaches needs to be designed in toria. Logistical support was provided by S Henry, kilometresratherthanmetresinordertomake DEPI,Orbost.TheauthorsthankKathyHimbeckfor any meaningful assessment ofthe species’ sta- producing the map showing survey locations, and HayleyDavis,JordandeJong,JakeUrlusandJacques tusatasite.Thepresent surveyaddressedthese Cop for their assistance in the field. Surveys were sampling issues, and targeted habitats most undertaken under Department ofSustainabilityand likelyto favourthespecies. Environmentresearchpermitnumber 10005694. In conclusion, M. balbus has suffered a sub- References stantial decline in both distribution and abun- AnstisM(2002)TadpolesofSouth-easternAustralia.AGuide dance in Victoria over the past 30 years. It is withKeys.(ReedNewHolland:Sydney) quite likelythat thespecies isextinctin Victo- BeArgAe,rGIo,gSgpienarCeL,R,SlDoacsozmabkeP,K,EaRralgGarneeMnA,D,llCyuatntniAnDg,hMacm-, ria; however, this is not certain. Some streams Donald KR,Hines HB,Lips KR, MarantclliGandParkes with potentially suitable habitat have not yet H (1998) Chytridiomycosis causes amphibian mortality associated with population declines in the rainforests of been surveyed thoroughly enough to make AustraliaandCentralAmerica.ProceedingsoftheNational this assessment with anyconfidence. In recent AcademyofSciences95,9031-9036. BickfordD.HowardSD,NgDJJandSheridanJA(2010)Im- years, three Australian amphibian species that pactsofclimatechangeontheamphibiansandreptilesof had ‘disappeared’ (Hero etal 2006), and were Southeast Asia. Biodiversity and Conservation Published presumed extinct, have been rediscovered: Cloenmlainnen2NFeabnrduaGirlyle2s0p1i0eGDO(I201120.)1R0e07s/psoln0s5e3t1o-‘0A10ca-l9l7r8e2c-o4r.d Litoria lorica in the Wet Tropics (Hoskin and ot the Southern Barred FrogMixophyes balbusfrom East Hero 2008); L castenea on thesouthernTable- Gippsland’ by Urlus and Marr. 77/e Victorian Naturalist lands of NSW (D Hunter unpublished data); Da1l2y9,G12(01-91928)1.Review oflhe status and assessment ofthe andL.piperata astream-breedingspeciesfrom habitat ofthe Slultering Frog Mixophyes balbus (Anura: northern NSW,(S Donnellan South Australian MHyeorbpaettroafcaluvniada2e8),2o-n11t.hesouthcoastofNewSouthWales. Museum,pers.comm.). Inallcasestheseredis- DalyG,PennayMandCoombesD(2000)Targetedsurveys coveries reflected a previous lack ofadequate cfoorastthoefSNteutwteSroiuntghFWraolg,es.MiUxnoppuhbyleisshbeadlbruesp,orotntothtehesoNuetwh surveyeffort,ratherthanarecovery.Relictpop- SouthWalesNational ParksandWildlifeService. ulations ofother threatened species, including DSL(2009)FloraandFaunaGuaranteeActionStatementfor theSouthern Barred Frog Mixophyes balbus. Department some populations ofM. balbus in NSW, have otSustainabilityandEnvironment,Melbourne,Victoria. persisted despite their vulnerability to Bd. It is DSVEict(o2r0i1a3)-2A0d1v3i.soDreypaLristtmeofntThorle'aStuesnlaeidnaVbeirltietbyraatnedFEnavuinraoni-n therefore possible that remnant populations of ment,EastMelbourne. M. balbusmaystillpersist inVictoria. Duellman WEandTruebI.(1994) BiologyofAmphibians.2 East Gippsland has been the stronghold GilEldens.pi(eJoGhRnH(1o9p9k9i)nsSuUrnvievyerosfittyhePrDeisss,trBiabluttiimoonrae)ndHabitat of many of Victorias threatened amphibian of the Booroolong Frog Litoria booroolongensis on the species, including the Giant Burrowing Frog SSoouutthh-wWealsetse.rnUnSlpoupbelsisohfetdhereGproeratttDoivNiSdiWngNRaatinognealinPNarekws Heleioporus australiacusy Green and Golden andWildliieService,SouthernZone,Queanbeyan.Arthur Bell Frog L. aurea Large Brown Tree Frog L. RylahInstitute,DepartmentofNaturalResourcesandEn- vironment,Heidelberg,Victoria. littlejohni, Stuttering Frog M. balbus, Martin’s GillespieGR(2002) EcologyoftheSpotted Tree FrogLito- Toadlet Uperoleia martini and Tylers toad- riaspenceri An investigation ofcausesofpopulation de- let U. tyleri. Currently these species are pos- cPlairnkev.ilUlen.published PhDUresis, UniversityofMelbourne, sibly the most poorly known vertebrates in GillespieGRandHeroJ-M(1999)Tireimpactofintroduced 70 TheVictorianNaturalist ) i - Research Reports fish uponAustralianfrogsInDeclinesandDisappearances LemckertF,PotterM,SmithBandBruestT(1997)Recent omfeAnutstAruasltiraalniaF:roCgasn,bppe.rr1a3)1-144.EdACampbell(Environ- frercoomrdtsheosfotuhtehscooausttheorfnNSbaWr.reHderfpreotgof(aMuinxaop2h7y,e4s3-b4a5lh.us) GillespieGRandHinesHB(1999)Thecurrentstatusoftem- LipsKR,BremF,BrenesR,ReeveJD,Alford RA,VoylesJ, perate riverine frogspecies insouth-eastern Australia. In CareyC,LiveL,PessierAPandCollinsJP(2006)Emerg- DeclinesandDisappearancesofAustralianFrogs, pp. 109 inginfectious diseaseand the loss ofbiodiversity in a 130.EdACampbell(Environment Australia:Canberra) Neotropical amphibian community. Proceedings ofIhe Gillespie GR and Hollis G (1996) The distribution and NationalAcademyofScience103,3165-3J70. habitatofthe Spotted Tree Frog, Litoriaspencer Dubois l.ugg A, Marsh P and Bartlett A (1993) Statement ofRe- (Anura: Hylidae),andanassessmentofpotentialcausesof sources, Usesand Values, EastGippslandForestManage- populationdeclines. WildlifeResearch23,49 75. ment Area. (Department ofConservation and Natural GillespieGR,ScroggieMRRoberts1),Coggerf1,McDonald Resources:Melbourne) cKoRnsaenrdvaMtaiohnonasyseMsJsm(e2n0t1s:1)ATuhsetrianlfilaunenfcreogosfausncaecratsaeinsttyudoyn. MaMhoounntyaiMnJsa(r1e9a93o)ftThheecesnttartaulscooafstfroofgsNeinwtShoeutWhaWtaalgeasn. BiologicalConservation 144, 1516-1525. In:HerpetologyinAustralia:aDiverseDiscipline,pp.257- HeroJ-MandGillespieGR(1993)'Ihetadpoleofthe Leaf- 264. (Eds) D Lunneyand D Ayers. (Transactionsofthe green Tree Prog (Litoriaphyllochroa). 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HuTnrtoepircsD.((G2r0i0f1f)ithSuUrnvievyesrsaintdyPmuobnliitsohrinign:gGoofltdhrCeoaatsetn)edfrog StAuaSrLt,SFNi,scChhmaannsoDnLJaSn,dCWoaxllNeAr,RWY.oun(2g00B4)E.,SRtoadtursigauneds species in South-eastern NewSouth Wales between Oc- trendsofamphibiandeclinesandextinctionsworldwide. tober,2000 and March,200T Unpublished report to the Science306. 1783-1786. HuNntSeWrDNatainodnaGlilPlaerskpsieanGdRWi(l2d0l1ifI)eNSeartviiocnea.l Recovery Plan UrBlaursre]danFdroMgaMrirxoRph(y2e0s11b)alAhucsalflrroemcoEradstoGfitphpeslSaonudt.heTrhne forthe StutteringFrog Mixophyesbalhus. Department of VictorianNaturalist128,272-275. SustainabilityandEnvironment,Melbourne. White A (2000).Thestatusofthe barredriverfrogs,Mix- IUCN (2010) IUCNRedListofThreatenedSpecies. Version ophyesbalhusandMixophyesitcratusintheSydneyBasin 2010.4. <http://www.iucnredfist.org>. Downloaded on 27 Region ofNew South Wales. Biosphere Environmental October2010. ConsultantsPty.Ltd. Kriger KM, Pereoglou F and Hero J-M (2006) Latitudinal variationintheprevalenceandintensityofchytrid(Batra chochytrium dendrobatidis) infection ineastern Australia. ConservationBiology21,1280-1290. LauranceWE(2008)Globalwarmingandamphibianextinc- Received8August2013;accepted7November2013 tionsineasternAustralia.AustralEcology33,1-9. Ninety-nineYearsAgo Noteson EnglishandJapanesenewtsinVictoria ByH. W.Davey,F.E.S. (ReadbeforetheFieldNaturalists'ClubofVictoria, 14thDee, 1914.) With frogs and toads, with oneortwo exceptions, impregnation ofthe eggs takes place afterthey have been extruded bythe female,thesameas in mostofthe fishes, hutwiththetailed Bactrachians asnewts (UErgogd-ellaayintgheisimcparrreigen—datoinoninofmuthcehegthgessisamuseuamlalnynienrteransalwi.t..h other newts.Afemaleselects someaquatic plant forthe purpose thedenserthe better and placesa singleegg in a fold ofa leaf, hiding theegg asmuchaspossible from sight.The necessity forall thiscare isatonceapparent,asthe malesarcmost assiduousintheirsearchaltereggs,ofwhichfoodtheyareextremely fond,andonceaneggisdiscovered in a leafthis istornanddraggedatbythe male until at last itcanreach theegg,when,withonesnapof thejaws,theeggdisappears. Bothsexeswillalsogreedilydevourtheyounglarvae,anditisprobably this cannibalistictrait that prompts thefemaletolayhereggssingly, folded in leavesofwaterplants,andthe denserthese arethebettersuited forherpurpose, astheeggsarebetterhidden,andgreateropportunities forescapeareaffordedtothenewly-hatchedlarvae. From The VictorianNaturalistXXXI,pp. 135, 137,January7, 1915 Vol 131 (3) 2014 71