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larger valleys of Hoodoo and Sellars Creeks can <strong>be</strong>come fully inundated <strong>to</strong> 1-2 km in width.<br />

The higher plains, ridgelines and small oval wetlands (pans) on interfluves of the Balurga<br />

land system might <strong>be</strong>come saturated and filled from local rainfall, but they appear <strong>to</strong> <strong>be</strong><br />

rarely inundated by actual flood water from creeks. However, these remote sensing data are<br />

also masked by forest <strong>cover</strong> > 30% in these areas (Figure 57).<br />

The remotely-sensed distribution of floodwater was also compared <strong>to</strong> the remotely-sensed<br />

distribution and dry-season visual clarity of both large “lacustrine” lagoons <strong>with</strong> permanent<br />

water (billabong, oxbows, lakes) and smaller “palustrine” wetlands <strong>with</strong> intermittent <strong>to</strong><br />

permanent water (pans, de<strong>pre</strong>ssions, swamps, bogs, marshes). The distribution (but <strong>not</strong><br />

clarity) of small palustrine wetlands > 0.2 ha was mapped by DERM (Queensland<br />

Department of Natural Resources (QDERM) 2010). For more permanent wetlands,<br />

(Lymburner and Burrows 2008) analysed Landsat TM satellite imagery <strong>be</strong>tween 1986 and<br />

2005 across the Northern Gulf area. They mapped the distribution of both lacustrine lagoons<br />

and larger palustrine wetlands (in-channel and off-channel) that contained open water and<br />

typically do <strong>not</strong> dry out in the dry season. During each dry season year for the period, they<br />

estimated the visual clarity (via colour) of the water body using the green-band digital num<strong>be</strong>r<br />

from Landsat, correlated <strong>to</strong> some secchi depth measurements of light penetration and water<br />

clarity. They classified clarity along a range <strong>be</strong>tween very clear and always turbid (Figure<br />

57).<br />

Comparing the distribution of flood waters <strong>to</strong> the distribution of lacustrine and palustrine<br />

wetlands demonstrates that most of the wetlands located along major creek and river valleys<br />

in Quaternary alluvium are regularly inundated (Figure 57). This is in contrast <strong>to</strong> the<br />

numerous palustrine wetlands on ridgelines, interfluves, and higher plains of the area that<br />

are <strong>not</strong> frequently flooded by creeks, but rather filled locally by rainwater and perhaps<br />

groundwater.<br />

Wet season water clarity, turbidity, or sediment concentrations measurements (or even<br />

remotely sensed estimates) are <strong>not</strong> available for the area, and should <strong>be</strong> a priority in future<br />

wet-season data collection. Comparisons of available dry-season clarity data (remotely<br />

sensed) <strong>to</strong> wet-season flood distributions suggest that wetland waterbodies along major flood<br />

paths in Quaternary alluvium are “usually turbid” during the dry season (Figure 57). This is<br />

likely due <strong>to</strong> 1) the abundance of silts and clays transported in the wet season along these<br />

paths that stay in suspension in<strong>to</strong> the dry season (colloidal clays), 2) the re-suspension of<br />

silts and clays in the dry season due <strong>to</strong> wind or local animal disturbance (cattle, pigs)<br />

concentrated along the banks of water bodies, and/or 3) the greater availability of nutrients<br />

for primary production (algae phy<strong>to</strong>plank<strong>to</strong>n) along major watercourses, which all reduce<br />

water clarity. In contrast, wetland water bodies that are adjacent <strong>to</strong> or outside of major flood<br />

paths are typically “clear <strong>to</strong> turbid”, “usually clear”, or “always clear”, such as <strong>to</strong>ward the edge<br />

of Quaternary valleys or on higher elevation terraces or tertiary sediments. Sediment and<br />

nutrient delivery <strong>to</strong> these wetlands may <strong>be</strong> lower or local hydrogeologic fac<strong>to</strong>rs may influence<br />

the delivery or filtration of sediment and nutrients. For example, sand bars lying along the<br />

main Alice and Mitchell River channels filter out finer particulate matter during the dry<br />

season base discharge, keeping in-channel pools clear in the dry season that <strong>be</strong>come turbid<br />

in the wet season (Figure 57).<br />

On Oriners Station, locally important lagoons (Figure 4) such as Mosqui<strong>to</strong> Lagoon along<br />

Eight Mile Creek were mapped as “usually turbid”. In addition, Horseshoe Lagoon lying along<br />

a tributary next <strong>to</strong> Crosbie Creek was classified as “usually clear”, despite this location <strong>be</strong>ing<br />

inundated by floods 4 times out of 7 years. Oriners Lagoon unfortunately was <strong>not</strong> mapped or<br />

classified, due <strong>to</strong> omissions or errors. These important errors and omissions in the remotely<br />

sensed data indicate the need for ground validation and cross-referencing <strong>with</strong> data from<br />

knowledgeable local people. Improvements in the understanding and management of these<br />

important wetlands requires the combination of local knowledge and data <strong>with</strong> appropriate<br />

field hydrology techniques, as well as the data provided by new scientific <strong>to</strong>ols such as<br />

remote sensing.<br />

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

150

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