Flora and Fauna Guarantee Act1988

Action statement No.47

Flora and Fauna Guarantee Act1988

Australian Anchor Plant / Hairy Anchor Plant Discariapubescens

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Action Statement No.47

Australian Anchor Plant / Hairy Anchor Plant Discariapubescens

Description

The Australian Anchor Plant, or Hairy AnchorPlant (Discaria pubescens (Brongn.) Druce), is adensely- branched, spiny shrub that grows to around 1 min height. Plants are often multi-stemmed atground level or may produce a main trunk that canreach

a diameter of 15 cm (Humphries 1993). Theleaves are short-lived, so plants are virtually leafless,with stout spines up to 4 cm long. Flowers aresmall (approximately 3 mm long) and white withfive sepals and five petals and occur at the base ofthe spines either solitary or in few to manyflowered clusters (10–50 flowers). Flowers are producedfrom November to January. The seeds are producedin small lobed capsules, 4-5 mm in diameter(Walsh and Entwisle 1999). They are brown, shinyand numerous and are dispersed by explosive splittingof the capsule (Hall and Parsons1987).

Distribution

The Australian Anchor Plant formerly hada widespread distribution in all easternAustralian states. It has not been recorded in Queenslandsince 1898 (Willis 1955) and is consideredendangered

in Tasmania (Coates 1991) and in NewSouth Wales (Harden 1990). In Victoria, the speciesis now restricted to fragmented populations inthe eastern highlands and to the west ofMelbourne (Willis 1973, Beauglehole 1980, AVH 2014).The

easternVictorianpopulationsarescatteredthrough the Snowy Range, Benambra,Wulgulmerang, Cobberas and Bendoc areas (Walsh andEntwisle 1999). Populations were previously recordedfrom the Delatite area, near Mansfield in 1853, buthave not been recorded there since 1895 (N.Walsh

Australian Anchor Plan / Hairy Anchor Plant(DELWP)

pers. comm. 2008). It was also formerlyknown from the Wodonga and Mitta Mitta areas(Walsh and Entwisle 1999). In western Victoria,small populations and individual plants occur alongthe Campaspe River (north of Kyneton), alongBirch Creek (at Smeaton and near Clunes) and on LalLal Creek and Moorabool River West Branch (nearLal Lal Reservoir). In western Victoria mostpopulationsare critically low in numbers. The populationsin eastern Victoria are larger. Severalpopulationsoccur in the Bendoc Nature ConservationReserve, the largest consisting of up to 500 plants (K.Seaton pers. comm.2010).

Habitat

The Australian Anchor Plant usually occurs ingrassy open woodlands and forests in the east ofVictoria (Hall and Parsons 1987) and in stream andriver valleys in western Victoria (Lunt 1987). Inwestern Victoria, it typically occurs in high rainfall areason rocky, basalt-based soils. In the easternhighlands, plants are usually associated with basalticsubstrate near streams, in cool, elevated areas (Walshand Entwisle 1999). Occasionally populationsoccur some distance from drainage lines and streams(K. Seaton pers. comm.2010).

Life History andEcology

Lunt (1987) and Humphries (1993) reportedthat seedlings of Australian Anchor Plant have notbeen recorded in the wild in Victoria, despitedetailed surveys over many years. However, morerecently several seedlings were found at WindmillBridge, following weed control work (B. Smith pers.comm. 2010) and at Bendoc (A. Trumbull-Wardpers.

Distribution in Victoria (DELWP,2015)

comm. 2008). The rarity of seedlings is notlikely to be due to problems with seed productionor germination (Hall and Parsons 1987). Viableseed has been collected from plants in westernVictoria and germinated readily in a glasshouse aftercold treatment (Humphries 1993). B. Smith(pers.

comm. 2008) found that seeds germinatedreadily, irrespective of treatment with heat, boiling wateror stratification. Very young and old seeds areslower to germinate and less viable (B. Smith pers.comm. 2008).

Hall and Parsons (1987) and Downe (pers.obs. 2007) report that mature plants resproutafter low intensity burns. B. Smith (pers. comm.2010)

observed that mature plants burnt by highintensity wildfire in 2009, along the CampaspeRiver,

had resprouted vigorously. However,seedlings transplanted to the area in 2007 showed only10% survival. The Bendoc area was burnt by wildfirein 2003. Post-fire surveys indicated thatAustralian Anchor Plant successfully regenerated, howeverthe size of monitored populations reduced byalmost half between 2004 and 2007. This may be dueto theeffectsofdroughtconditions(A.Trumbull-Ward pers. comm.2007).

Plants are known to have a life span exceeding30 years (Humphries 1993) and possibly up to 60years (B. Smith pers. comm. 2008). Willis (1955)noted that the general trend for most naturalpopulationshas been a reduction in plant number asmature plants senesce anddie.

Conservationstatus

Victorian conservationstatus

The Australian Anchor Plant is listed asthreatened under the Flora and Fauna Guarantee Act1988.

The Australian Anchor Plant is consideredrare in Victoria according to the Departmentof

Environment, Land, Water and Planning(DELWP)’s

Advisory List of Rare or Threatened Plants inVictoria

- 2014 (DEPI2014).

Threats

Grazing by stock, predominantly cattle(Bos taurus) and sheep (Ovis aries), and byintroduced herbivores, particularly Europeanrabbits (Oryctoloagus cuniculus), European hares(Lepuseuropeaus) and feral horses (Equuscaballus), poses a major threat, especially as themajority of plants grow where such animalscommonly graze (roadsides, paddocks and watercourses).

Competition by exotic species is of seriousconcern for all populations. Habitat loss andaccidental damage during weed eradication programsor construction and maintenance work(especially roadsides and streams) are ongoing issues.Some populations have recently been burnt bywildfire. The effect of inappropriate fire regimes(intensity, season or frequency) on long term survival isnot known and may be exacerbated by climatechange. Also of concern is erosion of road batters,especially in the Bendoc area, and stream banks particularlyto the west of Melbourne. It has been observedthat unseasonal frosts have severely burnt plants inthe Bendocarea.

Standardthreat / Source ofthreatExplanation
Competition / Invasionby environmental weeds / Weeds are a widespread and ubiquitous problem inthe habitat of the Australian Anchor Plant. They impact onthe species by competing for moisture, nutrients and light.Annual and perennial grasses are problematic at all sites.Other common environmental weeds are Gorse (Ulexeuropaeus), Blackberry (Rubus spp.), Hawthorn (Crategus spp.) andWillow (Salix spp.). Needle grass (Nassella spp.) may pose a threatat Turpins Falls (B. Smith pers. comm.2008).
Geneticdecline / Genetic decline- other / Willis (1955) noted that insufficient germination andjuvenile recruitment had been evident for many years. Asmature individuals senesce and die, they are not beingreplaced, causing local extinctions of populations (Willis 1955).This trend is stillcontinuing.
Habitat damageor loss / Land usechanges
- cultivationand construction / Vegetation clearance is an ongoing potential threat asmany populations occur on private land or unprotected publicland (road sides, state forest and public waterfrontages).
Habitat damageor loss / Vegetationcontrolactivities(incl. slashing and mowing) / Roadside slashing may result in accidentaldestruction,especially where plants are obscured by exotic speciesof similar appearance, such as Gorse and Hawthorn. Inthe Bendoc area many populations occur onroadsides.
Soilerosion / Erosion of road batters, especially in the Bendoc area,and stream banks, particularly to the west of Melbourne,may threaten plants growing in these habitats. Eventhough grazing in the Alpine National Park ceased in 2005,erosion causedbycattlegrazingmaystillbeaffectingpopulations(Humphries 1993).
Animals - domesticstock andintroduced herbivores / Trampling of plants may occur by large hoofeddomesticanimals, such as cattle, sheep and goats (Capra hircus),in association with grazing. Deer (Cervidea spp.), feralhorses and feral goats also causetrampling.
Herbivory / Animals - domesticstock / Populations are exposed to grazing and browsing bycattle,sheep and goats. In western Victoria, most populationsoccur on private land where livestock may be present orpublic water frontages which maybe grazed under licence. In partsof eastern Victoria, roadside grazing is common, especiallyover drought years. Grazing occurs in state forest and,although prohibited in the Alpine National Park, stock may wanderin from the adjoining stateforest.
Animals - introducedherbivores / Introduced herbivores, including rabbits, hares, feralhorses, goats and deer are known to graze Australian AnchorPlants. Rabbitsposeamajorthreattoplantsregeneratingafterfire along the CampaspeRiver.
Animals -native herbivores / PlantsatTurpinsFallshavebeengrazedbymacropods,most likely Swamp wallaby (Wallabia bicolour) andKangaroo (Macropus spp) (B. Smith pers. comm.2015).
Humandisturbance / Agricultural chemicals/ effluent / Accidental destruction of populations of AustralianAnchor Plant has occurred in some areas during weederadicationprograms, following misidentification with similarlooking weed species (in particularGorse).
Herbicide or pesticide spray drift may harm plantsduring weed or pest animal eradicationprograms.
Construction/maintenance- road, rail orutility / Grading road verges and dumping of soil is a problem inthe Bendoc area, where some populations have beendestroyed.
Weather / Weather- temperatureextremes / Plants have been severely burnt followingunseasonable frosts,intheBendocarea(A.Trumbull-Wardpers.comm. 2007).
Inappropriatefire regimes / Fire -intensity / Many plants were burnt in 2003 in eastern Victoriaand populations along the Campaspe River, nearRedesdale were burnt in 2009 . In the wild, this species dependson
resproutingforpost-fireregeneration.Intensefireorfrequent burning could damage or destroy the rootstock. Burningat inappropriate times of the year may hinder or preventseed production. Seedlings have not been observedregeneratingafterfire.
Fire - seasonor time / Frequent burning could prevent vegetative regrowthfrom producingsufficientphotosyntheticcompoundsforstoragein the root system of mature plants. This may eventually leadto plant death. Seed production would also be preventedthus affecting potential seedlingrecruitment.

Importantlocations

Catchment / Locationname / Landmanager / Bioregion
CORANGAMITE / Lal Lal Creekand MooraboolFalls / MooraboolShire / Victorian VolcanicPlain
EASTGIPPSLAND / Bendocarea / DELWP, East Gippsland Shire, VicRoads(VR) Parks Victoria(PV), Landholders / Victorian VolcanicPlain
BlackMountain Road -Limestone Road Intersection- Wombargo / PV / MonaroTablelands
CowombatFlat / PV / VictorianAlps
LimestoneCreek / PV / VictorianAlps
Nunniong PlainNatural Features andScenic Reserve - BigNunniong Plain / DELWP / VictorianAlps
Snowy RiverNationalPark / PV / MonaroTablelands
NORTHCENTRAL / Birch Creek,Clunes / Central HighlandsWater (CHW),Landholders / Victorian VolcanicPlain
Birch Creek,Smeaton / CHW,Landholders / Victorian VolcanicPlain
CreswickCreek / CreswickCreek / Victorian VolcanicPlain
HodgesBridge / Private / Victorian VolcanicPlain
MitchellsFalls / Private / Victorian VolcanicPlain
NORTHCENTRAL / Old KynetonHospital / Private / Victorian VolcanicPlain
QueensFalls / Private / Victorian VolcanicPlain
Turpins FallsNatural FeatureReserve / PV / Victorian VolcanicPlain
Windmill BridgeNatural FeatureReserve / PV / Victorian VolcanicPlain
NORTHEAST / Jim JackCreek / VR / Highlands - Northern Fall
Lake OmeoFlora Reserve, site A andsite B / Committeeof Management(CoM) / Highlands - Northern Fall
Lake OmeoWhite's Road / CoM / Highlands - Northern Fall
Spring Creek,near Cobungra / DELWP / VictorianAlps
Victoria River crossingA / DELWP / Highlands - Northern Fall

Past managementactions

ActionResultexplanation
Manageenvironmental weeds / Willows (Salix sp.) were removed along Lal Lal Creek prior to 2004 andshoots were treated by herbicide application (E. Swan pers. comm. 2008). Gorseand Hawthorn have been slashed at Windmill Bridge with hand cuttingoccurring near plants of Australian Anchor Plant. Parks Victoria has carried outhand weeding around original plants at Turpins Falls and Windmill Bridge.Herbicide controlwasdoneincloseproximitytoasampleofrevegetatedseedlings,with no negative impacts observed (B. Smith pers. comm.2008).
Erect/maintain fenceto exclude domesticstock / Fencing has occurred at the followingpopulations:
•in western Victoria at Lal Lal Creek (1988) (E. Swan pers. comm. 2008),Tur- pins Falls (1989), Birch Creek, Clunes (2004) and along the CampaspeRiver at Windmill Bridge (2008), Hodges Bridge and Queens Falls (on privateland) (2009) (B. Smith pers. comm.2013)
•ineasternVictoriaatLakeOmeoFloraReserve(sitesAandB)(1990’s)and Big Nunniong Plain (2010).
ThisactionhasbeeneffectiveatmostsitesinwesternVictoria(E.SwanandB. Smith pers. comm. 2015) but rabbit browsing is masking the effectivenessat sites in eastern Victoria (K. Seaton pers. comm.2015).
Protect habitat fromfire / At Lal Lal Creek, a burn was carried out in April 2006, to reduce the fuelload in the reserve adjacent to the fenced off Australian Anchor Plants. InMarch 2009, the opposite end of Lal Lal Creek reserve, close to the MooraboolFalls plant, was also burnt to reduce fuel (E. Swan pers. comm.2010).
Applyecological burning / Lake Omeo Flora Reserve was burnt in autumn 1986 resulting ingood regeneration (resprouting) of Australian Anchor Plant (C. Beardsellpers. comm. to S.C. Cropper Feb 1998 - VROTPop form P01717). Anecological burning trial was planned for the Bendoc Nature Conservation Reservein 2012-2013, to monitor the effect of fire on the Australian AnchorPlant.
However the area containing the target species did not burn. It hasbeen planned to burn this section in Autumn 2015 (Kerry Seaton pers. comm.2014)
Undertakedetailed populationmonitoringand collectdemographic information / Population monitoring has been undertaken asfollows:
•In western Victoria at Birch Ck Smeaton, Birch Ck Clunes, CreswickCk, Moorabool Falls, Windmill Bridge and Turpins Falls, where theoriginal plantsatmostsitesarestillpersisting.(B.SmithandE.Swanpers.comm. 2015).
•In eastern Victoria at several locations: 1. Spring Creek, Victoria Riverand Lake Omeo (2009 and 2015), 2. the Wombargo area and NunniongPlateau (2009 and 2015) and 3. the Bendoc area in 2007, 2010 and 2015 (J.Ricciar- dello pers. comm. 2010, K. Seaton pers. comm. 2015). In easternVictoria plantsarepersistingatalllocationsbutnotflourishingduetoseverebrows- ing by rabbits. It was noted that fruit set was low. It was also observedthat plants growing where rabbits are unable to browse appeared healthy(K. Seaton pers. comm.2015).
Control/reducehuman disturbance / Vegetation clearance at Cobungra Station ceased in 1998 and the sitewas rehabilitated.
Promotecommunity involvementprograms (eg. Land forWildlife, BotanicGuardians, Friendsgroups) / In 1994/1995, Ballarat Field Naturalists Club received funding under Adopta Plant scheme (now Botanic Guardians) to monitor populations ofAustralian Anchor Plant. In 2005/2006, Ballarat Environmental Network (assistedby DSEBallarat)receivedfundingfromtheCityofBallaratCrownLandGrantto undertakeenvironmentalweedcontrolworkatLalLalCreek.
Erect/maintain signsto restrict ordiscourage access / Vulnerable roadside populations of Australian Anchor Plant in theBendoc areaweresignpostedtoavoidaccidentaldestructioninJune2011.
Construct/maintaininformationboard / An information board describing the appearance of Australian AnchorPlant was prepared and displayed at Bendoc to assist landholders andweed contractorstodistinguishintroducedspeciessuchasGorseandEnglishBroom fromAustralianAnchorPlant.InformationsignswereplacedatTurpinsFalls and are in the process of being upgraded (B. Smith pers. comm.2013)
Liaise withprivate landholders / Prior to 1993, consultation with two land holders adjacent to BirchCreek occurred. Grants under the Save the Bush Scheme were made tothese landowners to assist with protection of plants. Fencing andmanagement agreements have been negotiated with private landowners nearHodges Bridge and seed has been collected from their properties, propagatedand replanted in-situ with landowner support (B. Smith pers. comm.2008).
Erect/maintainfence to excludeintroduced animals / TwoareasatWindmillBridgehavebeenfencedtoexcluderabbitsandprotect remnant individuals in preparation for reintroduction of AustralianAnchor Plant seedlings (B. Smith pers. comm. 2008). Fences were constructed in2010 at Big Nunniong Plain to exclude feral horses. The effectiveness of thisfencing ismaskedbytheeffectsofseverebrowsingbyrabbits(K.Seatonpers.comm. 2015).
Modifydomesticgrazingregimes / A grazing licence over uncommitted public land frontage on BirchCreek, Clunes was cancelled in 1991. Stock was removed from Windmill Bridgeand grazingpressurewasreducedintheLalLalCreekarea.Grazingwasprohibited intheAlpineNationalParkin2005.CattlewereremovedfromBendocNature Conservation Reserve in January 2011, to allow regeneration and growthof indigenousspecies.
Erect/maintaincages, / ThefencingatTurpinsFallswasupgradedin2008toexcludemacropods(B.
fences orother / Smith pers. comm. 2008). Fencing was upgraded at the Moorabool Falls sitein
structures toexclude / associationwithanewwalkingtrailthatallowsbettervisitoraccesstothesite
nativeanimals / (E. Swan pers. comm.2008).
Collectreproductive material / A small seed collection is present at the Victorian ConservationSeedbank, Royal Botanic Gardens Melbourne, Victoria. Seed viability tests indicateda germination rate of 75% (J. Jeanes pers. comm.2008).
Propagateseedlings / Priorto1989,seedwascollectedandpropagatedatCreswicknurseryfrom
and/or cuttingsfor / populations at Birch Creek and Lal Lal Falls (A. Arnold pers. comm.2008).
reintroductionor / Approximately 1,000 plants weregrown.
reinforcement / Since 2002 seed has been collected and propagated from remnantplants
growingatTurpinsFalls,downstreamofQueensFallsandnearHodgesBridge.
The single plant downstream of Queens Falls has not produced any seedsince
2007–itwasseverelyburntbywildfirein2009andhasresproutedvigorously,
but flowers have not been produced (B. Smith pers. comm. 2010).Plants
havealsobeensuccessfullypropagatedfromcuttingsinEastGippsland(J.
Ricciardello pers. comm.2010).
Establish andmaintain areintroduced/
translocatedpopulation / Seedlings have been planted in 15 localities in western Victoria,including Mooramong Nature Reserve, Creswick Creek and CarisbrookReservoir (Humphries1993).Morerecentlyplantshavebeenreintroducedintoseveral other west Victorian reserves including Turpins Falls, Windmill Bridge,Milking Yard SSR (Little Coliban River) and Kyneton Hospital (with varying success)(B. Smith pers. comm. 2015). Plants reintroduced at Lal Lal Creek andMoorabool Falls have not survived (E. Swan pers. comm. 2015). Two plants havebeen established and are currently fruiting in the Royal Botanic Gardens,South Yarra, Victoria (P. Milne pers. comm.2014)
Involvecommunity groups andvolunteers in recoveryactivities / In2007,anactivecommunitygroupformedanadvisorycommitteetooversee the Lal Lal Creek Reserve Management Plan, which includes theMoorabool Falls area. A Botanic Guardians grant has provided funds for the collectionand propagationofseedforreplantinginthereserve(E.Swanpers.comm.2008). In 2004 and 2007 local school children planted about 50 and 100seedlings respectivelyatTurpinsFallsandroughly120seedlingswereplantedin2008
at Windmill Bridge by Windarring community group (with approximately10% survival) (B. Smith pers. comm.2009).
Negotiatevoluntary acquisition orexchange of land / The Bendoc Nature Conservation Reserve was declared in 2001 fromthe purchase of 233 ha of private land by the Department of Sustainabilityand Environment (Robertson and Fitzsimons2005).

Conservationobjectives

Long termobjective

To ensure that the Australian Hairy Anchor Plant can survive, flourish and retain its potentialfor evolutionary development in thewild.

Objectives of this ActionStatement

•To maintain or improve condition ofhabitat

•To secure populations or habitat from potentially incompatible land use or catastrophicloss

•To increase the number of populations orindividuals

•To increase community awareness andsupport

•To increase knowledge of biology, ecology or managementrequirements

Intended managementactions

The intended management actions listed below are further elaborated in DELWP’s Actions forBiodiversity Conservation (ABC) system. Detailed information about the actions and locations, including priorities,is held in this system and will be provided annually to land managers and otherauthorities.

Standardobjective / Objectiveexplanation
To maintain orimprove
condition ofhabitat / Biomass of, and competition from, introduced species aremaintained
atlevelsthatenablenaturalregenerationofAustralianAnchorPlant,by herbicide treatment, weeding, slashing or ecologicalburns.
HerbivorylevelsarecontrolledsothatnaturalregenerationofAustralian Anchor Plantoccurs.
Ecologicalburningisundertakenatappropriateintensityandfrequency to preserve populations of the Australian AnchorPlant.
Habitat availability is maintained through the use of erosioncontrol works.
Standardaction / Details / Responsibleagents
Erect/maintain fenceto exclude domesticstock / Fence high priority populations or sections ofsuch populations (where plants are widelydispersed) from sheep, cattle and goats, where possible.In particular fence populations in theWombargo
and Bendoc areas and small populations alongthe Campaspe River, that were burnt in 2009. Cageany seedlings found in the firearea. / DELWP, PV,CoM,
Landholders
Erect/maintain fenceto exclude introducedand nativeanimals / Erect rabbit proof fencing aroundsignificant populations in eastern Victoria, inparticularthe Spring Creek and Victoria River Wombargo,
Nunniong Plain and Bendoc areas and inwestern Victoria at WindmillBridge.
Erect macropod proof fencing around plantsat TurpinsFalls.
Erect suitable fencing to deter deer andgoats whererequired. / DELWP,VR,
Shires, PV,CoM, Landholders