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at Oriners recently, including Sicklepod (Senna obtusifolia), Grader grass (Themeda<br />

quadrivalis) and other unidentified burr species. Neldner et al. (1997) <strong>not</strong>ed that Sicklepod<br />

was the most serious exotic weed threatening grassland communities on Cape York, while<br />

Grader grass was also rapidly invading roadsides and other areas distur<strong>be</strong>d by clearing or<br />

overgrazing.<br />

It is most likely that increased vehicle traffic associated <strong>with</strong> station access, pig hunting, new<br />

road construction, road maintenance and grading, and <strong>to</strong>urism have increased the s<strong>pre</strong>ad of<br />

weeds on<strong>to</strong> Oriners and Sef<strong>to</strong>n Stations. For example, at Oriners Station observations of<br />

Sicklepod, Grader grass, and other herbaceous weeds immediately around the homestead<br />

have <strong>be</strong>en brought in by vehicles and equipment <strong>used</strong> by both Indigenous and European<br />

people. New weeds have also <strong>be</strong>en recently observed along the newly bulldozed and<br />

enlarged road through Oriners. Additional weed dispersal also can occur down river and<br />

stream channels from upstream source areas, especially during flood. Feral animals such as<br />

pig and wild cattle are also known <strong>to</strong> s<strong>pre</strong>ad weed species across Cape York.<br />

Undoubtable, the new road and increased traffic through Oriners generally means that<br />

weeds may require more significant management action in the future <strong>to</strong> <strong>pre</strong>vent invasion and<br />

s<strong>pre</strong>ad. Local weed surveys on Oriners and Sef<strong>to</strong>n Stations are critically needed <strong>to</strong> plan for<br />

future management and address critical weed hotspots.<br />

3.3.4 Fire timing, frequency, and distribution<br />

Fire regimes are defined by the magnitude, frequency, duration, timing, and spatial patterns<br />

of fires through vegetation of grasslands and woodlands. Since European settlement and the<br />

introduction of cattle grazing on Cape York, traditional Indigenous fire regimes have <strong>be</strong>en<br />

replaced by regimes that are tailored <strong>to</strong>ward the production of cattle (Crowley 1995; Neldner,<br />

Stan<strong>to</strong>n et al. 1997; Crowley and Garnett 1998; Crowley and Garnett 2000). These regimes<br />

either reduce fire frequency by restricting burning, focus on burning fire breaks in the earlydry<br />

season <strong>to</strong> protect remaining feed and control cattle movement, and/or burn in the earlywet<br />

season (s<strong>to</strong>rm burns) <strong>to</strong> clear out old vegetation and residual weed biomass (Crowley<br />

1995; Crowley and Garnett 2000) . These fire regimes are different than those traditionally<br />

<strong>used</strong> by Indigenous people of Cape York, who utilized fire year round in a mosaic pattern<br />

across the landscape for game and vegetation management, but foc<strong>used</strong> their fire burning<br />

efforts across large areas in the early dry season or winter periods (Fensham 1997; Crowley<br />

and Garnett 2000).<br />

On nearby cattle stations <strong>to</strong> the east of Oriners and Sef<strong>to</strong>n (Artemis, Dixie, Musgrave, etc.)<br />

on central Cape York, Crowley and Garnett (Crowley and Garnett 1998; Crowley and Garnett<br />

2000) documented that changes in fire regimes or reduced burning <strong>be</strong>tween the 1960s and<br />

1990s resulted in woodland thickening as Melaleuca viridiflora (ti-tree) invaded <strong>pre</strong>viously<br />

open grasslands of wet meadows. Cattle grazing also shifted the dominance of grass<br />

species from <strong>pre</strong>ferred kangaroo grass (Themeda triandra) <strong>to</strong> black spear grass<br />

(Heteropogon con<strong>to</strong>rtus), along <strong>with</strong> other changes <strong>to</strong> <strong>pre</strong>ferred native grasses and invasion<br />

of exotic grasses and weeds. The combined influence of fire regime changes and intensive<br />

grazing <strong>pre</strong>ssure on grass species dominance and fuel load resulted in a net reduction<br />

grassland area by 10% <strong>be</strong>tween the 1960s and 1990s. The degree that similar changes have<br />

occurred at Oriners and Sef<strong>to</strong>n is unknown, but both currently and his<strong>to</strong>rically cattle num<strong>be</strong>rs<br />

were less on Oriners and Sef<strong>to</strong>n compared <strong>to</strong> stations further east and west.<br />

At Oriners and Sef<strong>to</strong>n Stations, the current fire regime for the last 15 years has <strong>be</strong>en<br />

dominated by frequent fires at least every other year (Figure 75) and hot late-dry season fires<br />

<strong>be</strong>tween Septem<strong>be</strong>r and Decem<strong>be</strong>r (Figure 76). The ignition source of these fires is<br />

unknown, but many appear <strong>to</strong> <strong>be</strong> unmanaged fires from either lightening strikes in the latedry<br />

season on<strong>to</strong> high fuel loads in largely un-grazed county, or fires mistakenly or<br />

deli<strong>be</strong>rately lit by people living or travelling through the area for various reasons (e.g., pig<br />

hunters). This area is somewhat anomalous compared <strong>to</strong> the rest of Cape York, where fire is<br />

managed more intensively in the late-dry season <strong>to</strong> eliminate fire completely or control fire<br />

using fire breaks or grazing management of fuel loads. Undoubtedly this fire regime is<br />

different than a traditional Indigenous regime that would have utilized early-dry season fires<br />

Working Knowledge at Oriners Station, Cape York<br />

173

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