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Serpentine National Park - Department of Environment and ...

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Management for Conservation<br />

The Darling Scarp Complex is restricted to a linear,<br />

north-south strip less than 2 km wide on the western<br />

edge <strong>of</strong> the Darling Plateau <strong>and</strong> is itself a unique<br />

geological feature. The Complex includes a diversity<br />

<strong>of</strong> vegetation communities <strong>and</strong> flora, ranging from<br />

w<strong>and</strong>oo woodl<strong>and</strong>s with mixes <strong>of</strong> marri through open<br />

forests <strong>of</strong> sheoak, heath, herb fields <strong>and</strong> lichens on<br />

granite rocks. Although well represented in<br />

conservation reserves, the area <strong>of</strong> Darling Scarp<br />

complex within the <strong>Park</strong> is, therefore, <strong>of</strong> regional<br />

importance.<br />

The Forrestfield Complex is dominated by open<br />

forest <strong>of</strong> marri-w<strong>and</strong>oo-jarrah on the heavier soils<br />

<strong>and</strong> marri-jarrah-sheoak on s<strong>and</strong>ier soils. It is<br />

estimated that only 3% <strong>of</strong> this complex remains<br />

uncleared <strong>and</strong> little is protected within conservation<br />

reserves. The block <strong>of</strong> this complex, which is located<br />

south <strong>of</strong> the Falls, therefore, has very high<br />

conservation value.<br />

Granite outcrops have a high conservation value,<br />

because <strong>of</strong> the diverse <strong>and</strong> unique fauna <strong>and</strong> flora<br />

communities associated with them. The granite<br />

communities are the last refuge <strong>of</strong> fire sensitive<br />

plants, some <strong>of</strong> which are quite rare/restricted<br />

(Hopper, pers. comm.). They are under some<br />

recreational pressure.<br />

Flora<br />

Two localised surveys <strong>of</strong> the <strong>Park</strong>'s flora have been<br />

completed. The WA Wildflower Society, in<br />

conjunction with CALM, established five flora plots<br />

in the Ridge Hill Shelf communities on the western<br />

edge <strong>of</strong> the <strong>Park</strong> in Spring 1994. CALM established<br />

several monitoring plots in the <strong>Park</strong> in locations that<br />

are representative <strong>of</strong> major vegetation communities.<br />

Recordings within these plots <strong>of</strong> species present,<br />

flowering <strong>and</strong> vertebrate fauna, were made during<br />

spring <strong>and</strong> autumn, 1990. Data from these plots show<br />

that some parts <strong>of</strong> the <strong>Park</strong> are floristically very rich,<br />

particularly in jarrah-sheoak forest. The two surveys<br />

will provide useful benchmarks for future research,<br />

however, further work is required.<br />

A new declared rare flora species, Lasiopetalum<br />

pterocarpum <strong>and</strong> two priority listed flora species:<br />

Pimelea rara (this species is now priority listed) <strong>and</strong><br />

Acacia horridula (Priority 3), have been found within<br />

the <strong>Park</strong>. In addition, two geographically restricted<br />

eucalypt species occur within the <strong>Park</strong>. Darling<br />

Range ghost gum (Eucalyptus laeliae) occurs on the<br />

sides <strong>of</strong> granite hills <strong>and</strong> is a feature on the hillsides<br />

above <strong>Serpentine</strong> Falls. salmon white gum<br />

(Eucalyptus lane-poolei) favours clayey soils on the<br />

scarp.<br />

The Wildlife Conservation Act (1950) protects all<br />

native flora <strong>and</strong> the declared rare flora is given<br />

special protection.<br />

18<br />

STRATEGIES<br />

1. Survey the <strong>Park</strong>'s vegetation <strong>and</strong> prepare<br />

detailed vegetation maps. (H)<br />

2. Systematically, over a period <strong>of</strong> five years,<br />

record the distribution, abundance <strong>and</strong> other<br />

details <strong>of</strong> the <strong>Park</strong>'s flora including threatened<br />

species. (M)<br />

3. Minimise the introduction, spread <strong>and</strong> impact<br />

<strong>of</strong> plant disease on native flora by<br />

implementing strategies in Sections Disease<br />

<strong>and</strong> Access. (H)<br />

4. Rehabilitate degraded vegetation communities<br />

in the <strong>Park</strong> (see Rehabilitation). (H)<br />

5. Use the established monitoring plots as long<br />

term reference areas. (M)<br />

6. Minimise damage <strong>and</strong> restrict access to herb<br />

fields on granite outcrops. (H)<br />

7. Exp<strong>and</strong> <strong>and</strong> maintain the <strong>Park</strong>'s herbarium.<br />

(L)

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