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<strong>Caboolture</strong> <strong>Water</strong> <strong>Quality</strong> <strong>Study</strong><br />

turbidity and conductivity and nutrients were monitored at all sites. Secchi depth and phytoplankton<br />

biomass was monitored at the canal sites, as were depth profiles for physico-chemical indicators.<br />

Toxicants in sediments were monitored at some sites in Saltwater Creek, Sheepstation Creek and<br />

Lagoon Creek.<br />

2.2 Environmental Protection Agency and Ecological Health Monitoring Program (EHMP)<br />

For the purposes of this study, the water quality data obtained from the EHMP program, a Healthy<br />

<strong>Water</strong>ways program, will not be distinguished from EPA water quality data (since the water quality<br />

component of EHMP is operated by EPA, ensuring that sampling techniques and quality assurance<br />

measures are identical). Although the EPA has been conducting water quality monitoring in<br />

Queensland since the 1970’s, only data collected since 1995 has been analysed in this study. Fiftyfour<br />

sites across Deception <strong>Bay</strong>, Pumicestone Passage and <strong>Caboolture</strong> River were monitored<br />

monthly. The indicators measured at each site are listed in Table 18 (Appendix A). Physico-chemical,<br />

nutrient, secchi depth and phytoplankton biomass (chlorophyll-a) indicators were monitored at most<br />

sites.<br />

2.3 The Pumicestone <strong>Region</strong> Coastal Monitoring Program (PRCMP)<br />

The Pumicestone <strong>Region</strong> Coastal Monitoring Program (PRCMP) was an NHT-funded Coast and<br />

Clean Seas Project for which water quality was monitored in Pumicestone Passage and its major<br />

tributaries since 1997. Fifty-eight sites (Appendix A) were assessed in this study for physico-chemical<br />

and secchi depth indicators. Nutrient concentrations were monitored at sixteen of those sites and are<br />

reported here.<br />

2.4 Other sources of data considered in this report<br />

Data types other than water quality were also considered in this study, including physical and<br />

biological attributes. Findings based on these other data types have not been summarised in this<br />

study, although they are referred to when appropriate. For a complete list of all data and information<br />

sources, please refer to the reference list.<br />

2.4.1 Prioritising stream regeneration works to protect and restore fish habitat.<br />

(Langdon, 2001).<br />

This ongoing project assesses stream condition by monitoring the structure of fish communities.<br />

Although a number of measures of fish community condition are generated only the overall site rating<br />

is considered in this study (Figure 23, Appendix F).<br />

2.4.2 Atlas of Natural Assets, Riparian and Reserve Vegetation, <strong>Caboolture</strong> Shire Council<br />

In 1995 CSC adopted the Atlas of Natural Assets (ANA, 1998), which documents remnant vegetation<br />

and plant diversity within the Shire. The Atlas provides essential information about the natural<br />

resources of the Shire to decision-makers, planners, developers and the general public. The<br />

assessment and mapping of riparian vegetation was updated in 1998 by WBM Oceanics Australia<br />

(Figures 24 and 25, Appendix G).<br />

2.4.3 State of the Rivers: Pumicestone <strong>Region</strong> Subcatchments, 2001<br />

The Pumicestone <strong>Region</strong> Subcatchments State of the Rivers report (SoR, 2001) provides a<br />

comprehensive assessment of the physical condition of rivers and streams of the region. Of relevance<br />

to this study are the assessments of the Northern Creeks, the <strong>Caboolture</strong> River, Lagoon Creek and<br />

Bribie Island. Attributes that were assessed in the SoR are presented in Table 1.<br />

8

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