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Caboolture Region Water Quality Study - Moreton Bay Regional ...

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<strong>Caboolture</strong> River Catchment<br />

Figure 7. Box plots of results for dissolved oxygen for sites in the <strong>Caboolture</strong> River. Refer to Appendix B,<br />

p. 54, for details on the interpretation of box plots.<br />

STP<br />

STP<br />

Weir<br />

Figure 8. Box plots of results for total nitrogen for sites in the <strong>Caboolture</strong> River. Refer to Appendix B, p.<br />

54, for details on the interpretation of box plots.<br />

Nutrient concentrations have increased over recent years at most estuarine sites (Table 5). An<br />

analysis of changes in water quality assessments suggested that at most sites between 4.8 km and<br />

17.1 km upstream, nitrogen (in all species) has increased (Table 5, Table 23). Some sites that had<br />

good water quality condition ratings for ammonia and total phosphorus in 2000 had poor condition<br />

ratings in 2001; this increase may represent a real increase in nutrient input to <strong>Caboolture</strong> River, or<br />

may be related to changes in laboratory techniques. The regression analysis of long-term trends<br />

indicated improving trends of secchi depth at many sites (Cab-1.6, Cab-7.6, Cab-15.1, Cab-18.8) and<br />

nutrients at sites near the river mouth since 1994. (For example, at site Cab-1.6 total phosphorus<br />

improved by 4% and ammonia by 21% annually; see Table 28 in Appendix F for full results).<br />

Regression analysis also indicated that pH has decreased at some of the estuarine sites since 1994,<br />

although the amount of change was small (Table 31, Appendix D).<br />

A comparison of water quality condition with previous years shows that most freshwater sites (CAB-<br />

1,2,3,4) have shown improvements in nutrients and that dissolved oxygen and turbidity have also<br />

improved at some sites (Table 5).<br />

The pattern of poor water quality at estuarine sites and better quality water at freshwater sites was<br />

also evident in a number of other physical indicators, including the size and integrity of riparian<br />

vegetation, reach environs, bank stability and channel diversity (Appendix, G, ANA, 1998; SoR, 2001).<br />

Similarly, some upstream sites in the <strong>Caboolture</strong> River have fish communities classed as being in<br />

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