Vegetation 51per 100 m 2 ). All <strong>of</strong> these vegetation units have been reduced by at least 90% (as estimated for vegetation <strong>of</strong>the eastern side <strong>of</strong> the Swan coastal plain as a whole by Government <strong>of</strong> Western Australian, 2000). Theremaining patches <strong>of</strong> this vegetation are threatened by clearing, weed invasion and frequent fire.The Corymbia calophylla – Kingia australis woodlands on heavy soils (FCT 3a) occur on a variety <strong>of</strong>landforms where shallow sand over mud aquitards perch rainwater and contribute to seasonal waterloggingin this vegetation. This FCT had a mean species-richness <strong>of</strong> 58.9 spp. per 10 m x10 m site in Gibson et al.(1994). Plant taxa that were almost always associated with this FCT in Gibson et al. (1994) were Banksiadallanneyi var. dallanneyi, Desmocladus fasciculatus, Kingia australis, Mesomelaena tetragona, Philothecaspicata and Xanthorrhoea preissii. Also present at high consistency levels in this unit were Borya scirpoidea,Cyathochaeta avenacea, Hakea ceratophylla, Pericalymma ellipticum and Synaphea petiolaris. Althoughsome <strong>of</strong> the taxa consistently present in FCT 3a may also be present in the two other Marri (Corymbiacalophylla) units (Table 5.2), each <strong>of</strong> these FCTs have been shown to have floristic and habitat factors thatclearly distinguish them from each other (English and Blyth, 2000a). There are approximately 83 ha <strong>of</strong> FCT3a remaining at 10 documented sites that are located at Pinjarra, Waroona, Byford, Mundijong, Wungong,Forrestfield and Kenwick (English and Blyth, 2000a). The Forrestfield occurrences <strong>of</strong> this TEC total 4.6 ha(4 ha and 0.6 ha in two reserves). The known Kenwick occurrence is 0.75 ha and is located in the BrixtonStreet Reserve (BFS 387).Table 5.2: Native taxa recorded in at least 50% <strong>of</strong> sites in the three Corymbia calophylla TECs <strong>of</strong> the Eastern SCP inGibson et al. (1994). (Taxa in 90% or more sites are underlined)Corymbia calophylla/Kingiaaustralis FCT 3ATreesCorymbia calophyllaShrubsBanksia dallanneyi var. dallanneyiHakea ceratophyllaKingia australisPericalymma ellipticumPhilotheca spicataSynaphea petiolarisXanthorrhoea preissiiHerbsBorya scirpoideaCassytha glabellaConostylis setigeraCyathochaeta avenaceaDampiera linearisDesmocladus fasciculatusDrosera menziesii subsp. menziesiiGoodenia caeruleaHaemodorum laxumHypolaena exsulcaMesomelaena tetragonaNeurachne alopecuroideaPatersonia occidentalisTetraria octandraThysanotus manglesianusTricoryne elatiorXanthosia huegelii.Corymbia calophylla/EucalyptusmarginataFCT 3BCorymbia calophyllaEucalyptus marginataAcacia willdenowianaBaeckea camphorosmaeBanksia dallanneyi var. dallanneyiBossiaea eriocarpaBurchardia umbellataGompholobium marginatumHibbertia hypericoidesXanthorrhoea preissiiBurchardia umbellataCaesia micranthaCaladenia flavaChamaescilla corymbosaConostylis junceaDesmocladus fasciculatusDrosera erythrorhizaDrosera stoloniferaHaemodorum laxumHomalosciadium homolocarpumHypolaena exsulcaKennedia prostrataLagenifera huegeliiLepidosperma angustatumLomandra hermaphroditaMesomelaena tetragonaPronaya fraseriSowerbaea laxifloraTetraria octandraThysantus thyrsoideusCorymbiacalophylla/Xanthorrhoea preissiiFCT 3CCorymbia calophyllaEucalyptus wandooAcacia pulchellaBanksia dallanneyi var. dallanneyiBurchardia umbellataGompholobium marginatumHypocalymma angustifoliumXanthorrhoea preissiiBurchardia umbellataCaesia micranthaCyathochaeta avenaceaDesmocladus flexuousDichopogon capillipesDrosera menziesii subsp. penicillarisLepidosperma sp. BJK & NG232Mesomelaena tetragonaNeurachne alopecuroideaOpercularia vaginataTetraria octandraTauss, C. and Weston, A.S. (2010). The flora, vegetation and wetlands <strong>of</strong> the Maddington-Kenwick Strategic Employment Area.A survey <strong>of</strong> the rural lands in the vicinity <strong>of</strong> the Greater Brixton Street Wetlands. Report to the <strong>City</strong> <strong>of</strong> <strong>Gosnells</strong>, W.A. Version 18.04.10
Vegetation 522. Shrublands and Woodlands on Muchea Limestone <strong>of</strong> the Swan Coastal PlainMuchea Limestone (ML), a geological unit also known as Plain Limestone (Gozzard, 1982), occurs on theeastern side <strong>of</strong> the Swan Coastal Plain. It occurs in a discontinuous distribution from Muchea to Bengeralong the eastern side <strong>of</strong> the Swan Coastal Plain.The known occurrences <strong>of</strong> the Muchea Limestone TEC currently include a range <strong>of</strong> wetland and welldrainedplant habitats, on a variety <strong>of</strong> landforms. Unlike many other TECs, that are defined primarily on thebasis <strong>of</strong> floristic composition (e.g. a single Floristic Community Type from Gibson et al.,1994), the MucheaLimestone TEC is defined as a range <strong>of</strong> relatively heterogeneous assemblages that inhabits a rare geologicalformation. The vegetation that has been recorded on Muchea Limestone includes Melaleuca huegeliishrubland, Eucalyptus decipiens mallee, Casuarina obesa woodland and Melaleuca spp. (M. brevifolia, M.systena, or M. viminea) shrublands (Keighery and Keighery, 1995). Calcicole species such as Eremophilaglabra, Eucalyptus decipiens, Eucalyptus gomphocephala, Gahnia trifida, Grevillea curviloba, Grevilleaevanescens, Melaleuca brevifolia and Thysanotus arenarius can be present (Keighery and Keighery, 1995;English and Blyth, 2000b; B.J. Keighery, pers. comm.). Muchea Limestone vegetation was not sampled byGibson et al, (1994) and/or not identified as a distinct FCT in that study. Floristic analyses <strong>of</strong> vegetation <strong>of</strong>the eastern SCP that are conducted against the SCP database <strong>of</strong> Gibson et al, (1994) <strong>of</strong>ten group MLvegetation with the FCTs <strong>of</strong> Tamala Limestone in the Spearwood Dunes or FCT 18 (Shrublands onCalcareous Silts) due to the calicole species common to all <strong>of</strong> these vegetation types (English and Blyth,200b).The range <strong>of</strong> flora and vegetation that occurs in Muchea Limestone and the habitats <strong>of</strong> this TEC are, as yet,poorly documented. In addition to the generally high levels ( >90%) <strong>of</strong> loss and degradation <strong>of</strong> nativevegetation on the eastern SCP due to clearing and grazing(Government <strong>of</strong> Western Australian, 2000a, Table4, Pinjarra Plain), many occurrences <strong>of</strong> Muchea Limestone on the SCP have been extirpated by mining(Keighery and Keighery, 1995). There is little known about the aquifers that maintain this vegetation and thedevelopment <strong>of</strong> calcicole vegetation on the eastern SCP. There are no data available about the basiccharacteristics <strong>of</strong> these aquifers (e.g. fine scale maps <strong>of</strong> the aquifers or identification <strong>of</strong> the catchment areasthat maintain them) that could inform in the sustainable management <strong>of</strong> these ecosystems. The styg<strong>of</strong>aunathat potentially inhabit these aquifers have also not been investigated. Muchea Limestone and the biotaassociated with it are thus <strong>of</strong> high scientific and conservation significance.Muchea Limestone TEC occurrences are, as yet, poorly documented, but available data cite only twooccurrences south <strong>of</strong> the Swan River in the Perth Metropolitan Region. These are in BFS 465, SouthernRiver (Government <strong>of</strong> Western Australian, 2000) and in Cannington (; B.J. Keighery, pers. comm.).5.1.2 Vegetation <strong>of</strong> State Conservation SignificanceA search <strong>of</strong> the Threatened Ecological Communities Database <strong>of</strong> DEC (2008d) and searches <strong>of</strong> the literature(including Trudgen and Keighery, 1995 and Government <strong>of</strong> Western Australian, 2000) showed that, apartfrom the two EPBC listed TECS (as above), occurrences <strong>of</strong> another seven TECs that are listed by theWestern Australian Department <strong>of</strong> Environment and Conservation (Table 5.3) have been recorded inCannington, Forrestfield, Kenwick, Maddington, Orange Grove, Queens Park, Southern River, Welshpooland Wattle Grove. There were no Priority Threatened Ecological Communities (PTECs) listed by DEC(2008d) for this area.The seven TECS listed by DEC (2008d) have all been assessed and approved by the Western AustralianThreatened Species Scientific Committee, under the same international criteria that are used to determineTECS under the EPBC Act and thus they are, in a scientific sense, all <strong>of</strong> national conservation significance.However, these Western Australian-listed TECs are yet to be endorsed by the Federal Department <strong>of</strong>Environment, Water, Heritage and the Arts for EPBC listing.Tauss, C. and Weston, A.S. (2010). The flora, vegetation and wetlands <strong>of</strong> the Maddington-Kenwick Strategic Employment Area.A survey <strong>of</strong> the rural lands in the vicinity <strong>of</strong> the Greater Brixton Street Wetlands. Report to the <strong>City</strong> <strong>of</strong> <strong>Gosnells</strong>, W.A. Version 18.04.10