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3.2.10.6 Summary of Water and Sediment Processes at Oriners Lagoon<br />

The size and volume of Oriners, its importance for residential purposes and the complexity of<br />

the controls on water and sediment inputs and outputs, meant that a conceptual model was<br />

created <strong>to</strong> visualize the major fac<strong>to</strong>rs and their interactions (see Figure 86 in Part 4). The<br />

main independent controller on the water volume of Oriners is the climatic input of rainfall<br />

and resultant runoff. Rainfall can vary annually, seasonally and daily (Figure 44; Figure 45;<br />

Figure 46) and influence rainfall-runoff patterns and vegetation <strong>cover</strong>, <strong>with</strong> the latter in turn<br />

mediating runoff from rainfall. Land use impacts such as grazing, fire, weed invasions and<br />

roads can also influence vegetation <strong>cover</strong>, which in turn mitigate water and sediment runoff<br />

volumes in response <strong>to</strong> rainfall. The main inputs of water for Oriners Lagoon are from the<br />

Eight Mile Creek anabranches (Figure 64; Figure 66), small tributaries and gullies off the<br />

Holroyd Plain, and combined baseflow and groundwater (GW) input. The main sediment<br />

sources <strong>to</strong> Oriners Lagoon are also Eight Mile Creek anabranches (Figure 68; Figure 69), but<br />

sediment sources from gully and road erosion are increasing due <strong>to</strong> local land use impacts<br />

(Figure 69ef; see Section 3.2.11 on gully erosion <strong>be</strong>low).<br />

Downstream fac<strong>to</strong>rs also influence the water volume and s<strong>to</strong>rage of Oriners Lagoon by<br />

controlling the outputs of water. Evaporation and transpiration (combined as<br />

evapotranspiration, ET) are key natural processes that slowly draw down the water volume in<br />

the lagoon over the dry season. Evaporation likely dominates <strong>to</strong>tal ET, but the transpiration<br />

of lagoon water by trees in<strong>to</strong> the atmosphere could also <strong>be</strong> locally significant. Additional<br />

pumping <strong>with</strong>drawals are made by the human use of Oriners station. At <strong>pre</strong>sent these<br />

<strong>with</strong>drawals are minuscule, but could increase in the future <strong>with</strong> more development. The<br />

height of the outlet sill of the lagoon (Figure 70) is the key fac<strong>to</strong>r that controls the <strong>to</strong>tal water<br />

s<strong>to</strong>rage volume of the reservoir, in addition <strong>to</strong> the volume of floodwater and baseflow output.<br />

Different types of vegetation growing on the sill, in addition <strong>to</strong> LWD, can influence the sill<br />

roughness and stability. Native perennial grass is likely <strong>be</strong>ing a <strong>be</strong>tter stabilizer of soil across<br />

the entire sill, rather than trees that funnel water in<strong>to</strong> discrete scour locations. Human land<br />

use of the local area around the lagoon outlet can have significant impacts on the erosion or<br />

deposition of sediment on the sill, specifically roads, gullying, and vegetation changes<br />

(Figure 70), which again in turn influence lagoon water volume. A big unknown is the degree<br />

that the sill height influences the flushing of sediment from the lagoon during floods, such as<br />

sand <strong>be</strong>dload. A lower sill height could allow for easier passage of sand, but a low sill high<br />

could also reduce water depth, turbulence and shear stress in the lagoon during flood, which<br />

promote local scour of the lagoon bot<strong>to</strong>m.<br />

3.2.11 Gully erosion<br />

3.2.11.1 Background on gully erosion<br />

Gully erosion is the process by which running water cuts new unstable channels in<strong>to</strong> erodible<br />

soils and regolith. Gullies are larger than rills, which can <strong>be</strong> ploughed or easily crossed, but<br />

smaller than streams, creeks, arroyos, or river channels. Gullying causes severe land<br />

degradation, is a major component of contemporary sediment budgets, and is a major source<br />

of sediment pollution <strong>to</strong> aquatic ecosystems. Two types of gully erosion are typically found in<br />

Australia, including Oriners and Sef<strong>to</strong>n Stations: 1) hillslope or colluvial gully erosion, and 2)<br />

alluvial or floodplain gully erosion (Brooks, Shell<strong>be</strong>rg et al. 2009).<br />

Hillslope gullies are generally located in headwater settings, where they erode in<strong>to</strong> colluvium<br />

(or alluvium mixtures), saprolite, weak sedimentary rock, or other weathered rock, and have<br />

also <strong>be</strong>en defined as valley-side or valley-head gullies. Their length is much typically greater<br />

than their width and their erosion mechanism is typically overland flow in which excess shear<br />

stress exceeds resisting forces (Brooks, Shell<strong>be</strong>rg et al. 2009).<br />

Alluvial gullies are incisional features entrenched in<strong>to</strong> floodplain or terrace alluvium typically<br />

<strong>not</strong> <strong>pre</strong>viously incised since initial deposition. They are often located adjacent <strong>to</strong> rivers or<br />

floodplain water bodies in the Mitchell-Alice catchment (Brooks, Shell<strong>be</strong>rg et al. 2009;<br />

Shell<strong>be</strong>rg 2011; Shell<strong>be</strong>rg, Brooks et al. 2012) . They are locally called “breakaways”, or<br />

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

165

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