City of Darebin Heritage Study Volume 1 Draft Thematic
City of Darebin Heritage Study Volume 1 Draft Thematic City of Darebin Heritage Study Volume 1 Draft Thematic
DAREBIN HERITAGE STUDY STAGE 28 DAREBIN’S NATURAL HERITAGEIntroductionThis chapter provides an overview of Darebin’s natural heritage in the present, in contrast tothe picture provided in Chapter 1 Creating Darebin, before the time of European arrival. Therange of activities and processes that have altered the environment are described in 4.5 Alteringthe environment. Moves to protecting and managing the environment are discussed in 5.5Creating public landscapes and 7.6 Appreciating and defending the environment. This chapterfollows the themes in the Australian Natural Heritage Charter of ecosystems, biodiversity andgeodiversity and provides a summary of Darebin’s natural heritage.8.1 Ecosystem valuesAccording to the Natural Heritage Charter, Ecosystem means a dynamic complex of organismsand their non-living environment, interacting as a functional unit.Most of Darebin falls into the Victorian Volcanic Plain bioregion, but the higher parts ofBundoora Park and Mount Cooper, and the LaTrobe University and Bundoora sections of themunicipality are part of the Gippsland Plain bioregion.Landscape structure and connectivityThe process of settlement of Darebin has changed the landscape from having multidirectionalconnections between a mosaic of ecosystems that extended across the whole municipality (andfurther) to one where small fragments of ecosystems remain, many completely surrounded bysuburbia.This fragmentation of the landscape has reduced its habitat values even more than suggested bythe massive reduction in the total area of natural ecosystems to an estimated 2%. According toBennett (1999):Habitat fragmentation is a dynamic process that has three main components: an overall loss ofhabitat in the landscape, reduction in the size of remaining blocks, and increased isolation bynew forms of land use. Changes to the pattern of habitats in the landscape result in changes toecological processes that in turn affect the status of the flora and fauna. Effects of habitatfragmentation on wildlife include: loss of species in fragments, changes to the composition offaunal assemblages, and changes to ecological processes that involve animals. Isolation of habitatsis a fundamental consequence of fragmentation. A range of evidence shows that isolation, and thedegree of spatial isolation, have negative impacts on many populations and communities. Thenegative effects of isolation are attributed to the decreased opportunity for movement of animalsto and from other habitats.While there is not a lot of evidence to demonstrate how effective habitat corridors can be, it issafer to assume that a connected landscape with corridors is preferable to a fragmentedlandscape. Anderson & Jenkins (2006) identify two basic types of corridors - the landscapecorridor which provides multidirectional connections between a mosaic of ecosystems thatextend over an area of tens to thousands of square kilometres, and linear or habitat movementcorridors which provide a single continuous (or near continuous) link between two or moreusually larger habitat blocks. The landscape corridor that Darebin was is no more. Manyremnant habitats are poorly connected if at all to other habitat areas, reducing their ability tomaintain animal and plant populations, especially over time. Some linear corridors remain, andthese should be protected and enhanced. There is much scope to re-create linear corridors atleast along the main waterways.Strategies to enhance the connectedness of habitats in Darebin should form part of Stage 5 ofthe Heritage Study.132
VOLUME 2: THEMATIC ENVIRONMENTAL HISTORYWaterwaysImpacts upon waterways in Darebin have included pollution, filling, vegetation removal, rockremoval, straightening, putting into channels and piping, as well as diversion of flows fromupstream.The Draft Regional River Health Strategy indicates:Merri Creek’s urban sections (including Edgars Creek) are listed as being in very poor condition,with very poor water quality, poor aquatic life, moderate habitat and stability, very poorvegetation, and poor flow. Its social value is listed as very high. Priorities include improvingwater quality and vegetation to poor, and habitat and stability to good.Darebin Creek’s urban section is in poor condition, with moderate water quality, poor aquaticlife, excellent habitat and stability, very poor vegetation and poor flow. Its social value is listed asvery high. Priorities include improving water quality from moderate to good.These findings are based on very few sampling points, and they should not be interpreted tomean that no parts of the waterways are in good condition, or worth protecting.Figure 92Merri Creek, Northcote[http://www.darebin.vic.gov.au/Page/images/OS_Merri_Creek.jpg]Grassy woodlandsThe Grassy woodlands in Darebin are now largely cleared and removed as a result of timberclearing, firewood cutting, grazing and urban development. Remnants still occur at BundooraPark, and the natural reserves set aside in the grounds at La Trobe University (Greswell ForestNature Conservation Reserve etc.). The conservation status of Grassy woodlands is wellsummarised by Robinson & Traill (1996):The temperate woodlands are the most threatened type of wooded ecosystem in Australia. Theyonce covered 10% of land in eastern and south-western Australia. Since European settlementmore than 80% of that area has been cleared of its former native vegetation for agriculture. Insome districts, more than 95% has been cleared much of what remains is grossly altered. Becauseof this destruction and alteration of most woodland habitat, the temperate woodlands nowcontain a very high number of threatened plants and animals....The Bioregional Conservation Status of Plains Grassy Woodland and Grassy Woodlands is‘endangered’, which is the most significant rating available (PPWCMA, 2006). Plains GrassyWoodland is listed under the Flora and Fauna Guarantee Act (as Western Basalt Plains [RiverRed Gum] Grassy Woodland Floristic Community 55-04) for protection (DSE, 2006).133
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DAREBIN HERITAGE STUDY STAGE 28 DAREBIN’S NATURAL HERITAGEIntroductionThis chapter provides an overview <strong>of</strong> <strong>Darebin</strong>’s natural heritage in the present, in contrast tothe picture provided in Chapter 1 Creating <strong>Darebin</strong>, before the time <strong>of</strong> European arrival. Therange <strong>of</strong> activities and processes that have altered the environment are described in 4.5 Alteringthe environment. Moves to protecting and managing the environment are discussed in 5.5Creating public landscapes and 7.6 Appreciating and defending the environment. This chapterfollows the themes in the Australian Natural <strong>Heritage</strong> Charter <strong>of</strong> ecosystems, biodiversity andgeodiversity and provides a summary <strong>of</strong> <strong>Darebin</strong>’s natural heritage.8.1 Ecosystem valuesAccording to the Natural <strong>Heritage</strong> Charter, Ecosystem means a dynamic complex <strong>of</strong> organismsand their non-living environment, interacting as a functional unit.Most <strong>of</strong> <strong>Darebin</strong> falls into the Victorian Volcanic Plain bioregion, but the higher parts <strong>of</strong>Bundoora Park and Mount Cooper, and the LaTrobe University and Bundoora sections <strong>of</strong> themunicipality are part <strong>of</strong> the Gippsland Plain bioregion.Landscape structure and connectivityThe process <strong>of</strong> settlement <strong>of</strong> <strong>Darebin</strong> has changed the landscape from having multidirectionalconnections between a mosaic <strong>of</strong> ecosystems that extended across the whole municipality (andfurther) to one where small fragments <strong>of</strong> ecosystems remain, many completely surrounded bysuburbia.This fragmentation <strong>of</strong> the landscape has reduced its habitat values even more than suggested bythe massive reduction in the total area <strong>of</strong> natural ecosystems to an estimated 2%. According toBennett (1999):Habitat fragmentation is a dynamic process that has three main components: an overall loss <strong>of</strong>habitat in the landscape, reduction in the size <strong>of</strong> remaining blocks, and increased isolation bynew forms <strong>of</strong> land use. Changes to the pattern <strong>of</strong> habitats in the landscape result in changes toecological processes that in turn affect the status <strong>of</strong> the flora and fauna. Effects <strong>of</strong> habitatfragmentation on wildlife include: loss <strong>of</strong> species in fragments, changes to the composition <strong>of</strong>faunal assemblages, and changes to ecological processes that involve animals. Isolation <strong>of</strong> habitatsis a fundamental consequence <strong>of</strong> fragmentation. A range <strong>of</strong> evidence shows that isolation, and thedegree <strong>of</strong> spatial isolation, have negative impacts on many populations and communities. Thenegative effects <strong>of</strong> isolation are attributed to the decreased opportunity for movement <strong>of</strong> animalsto and from other habitats.While there is not a lot <strong>of</strong> evidence to demonstrate how effective habitat corridors can be, it issafer to assume that a connected landscape with corridors is preferable to a fragmentedlandscape. Anderson & Jenkins (2006) identify two basic types <strong>of</strong> corridors - the landscapecorridor which provides multidirectional connections between a mosaic <strong>of</strong> ecosystems thatextend over an area <strong>of</strong> tens to thousands <strong>of</strong> square kilometres, and linear or habitat movementcorridors which provide a single continuous (or near continuous) link between two or moreusually larger habitat blocks. The landscape corridor that <strong>Darebin</strong> was is no more. Manyremnant habitats are poorly connected if at all to other habitat areas, reducing their ability tomaintain animal and plant populations, especially over time. Some linear corridors remain, andthese should be protected and enhanced. There is much scope to re-create linear corridors atleast along the main waterways.Strategies to enhance the connectedness <strong>of</strong> habitats in <strong>Darebin</strong> should form part <strong>of</strong> Stage 5 <strong>of</strong>the <strong>Heritage</strong> <strong>Study</strong>.132