Water Quality

 

Turbidity

Turbidity within the Lake Eyre and Bulloo province is generally high, but can be low at upland or headwater sites.  At lowland sites, turbidity remains high even during the sometimes long periods between flows (Bailey, 2001; Bunn et al., 2003).  Average visibility measurements (secchi disc depths) from the Lake Eyre Basin rivers show visibility to be variable between catchments and over time, although there is a slight gradient of decreasing variability and turbidity moving westwards (Bailey, 2001).  For more eastern rivers (Thomson and Barcoo Rivers) the average visibility depth is around 6cm (range variable with river 0.1 - 28 cm) and western rivers; mid reaches 4 cm and lower reaches 6cm (range variable with river 1 - 12 cm) (Bailey, 2001).  Dispersive soil types and runoff patterns are contributing factors to turbidity in this province (Bailey, 2001).


Information about primary productivity and light climate

Information about methods

 

  Mean SE Max Min
Turbidity (NTU) 359 31 1000 4
Photic Depth (cm)* 25.9 2.4 75 10

* source Bunn et al., 2006

Photic depth

Light penetration of the water column or photic zone depth is shallow, reflecting the high turbidity of the system.  Light is one factor governing rates of in-stream primary production because the growth of most aquatic plants is limited by light availability.  Photic depth has been determined for 15 waterholes in the Cooper Creek catchment, shown below, and these results show that incident light can be measured at slightly deeper depths in this system compared with the Murray-Darling province (Bunn et al., 2006).

Benthic metabolism

Arid zone streams and rivers are more metabolically active than temperate systems, with gross primary production one to two orders of magnitude greater (Bunn et al., 2006).  Rates of benthic metabolism in the Lake Eyre and Bulloo province have been recorded for dry season habitats and on the inundated floodplains of the Cooper Creek system.  During the dry season, a prominent band of epipelic algae in the littoral zone of waterholes has been found to be highly productive.  The productivity of littoral zone algae is so prolific that despite low productivity in the deeper water column due to light extinction and only a limited area of littoral zone habitat (< 10%), these waterholes have been found to be net producers of carbon (Bunn et al., 2003).  Rates of primary production associated with phytoplankton can also occasionally be high in the surface waters of these turbid systems, rates ranging from 1.5 mg C L-1 day-1 to 500 mg C L-1 day-1, have been measured during extended periods of no-flow (Bunn et al., 2006).  During inundation of the vast floodplains of the Cooper Creek system warm, slow-flowing waters transform the terrestrial landscape into a shallow ‘lake’ with productivity increasing with inundation time (Davies et al., 2003).

 

    Mean SE Max Min

Littoral

Gross Primary Production (mg C m-2 day-1) 2235.59 223.030 4015 68
Respiration (mg C m-2 day-1) 1429.94 135.90 2462 101
Production/Respiration 1.53 0.082 1.93 0.67
Channel Gross Primary Production (mg C m-2 day-1) 38.47 5.28 88 10
Respiration (mg C m-2 day-1) 61.82 7.79 124 22
Production/Respiration 0.62 0.038 0.87 0.32

 

 

 

Last updated: 21 February 2012

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