The Wilson Inlet Catchment Committee Inc (WICC)

Wilson Inlet 5



Cover page

Introduction

Nutrients

Water Quality Cycle

Stratification

Water Quality

Comparative data

Summary of Findings

References

 

Water Quality in Wilson Inlet from 1995 to 2002

Summary of findings

To date the major findings of the water quality monitoring program have been:

  • Water quality in the Inlet is good for most of the year; compared both to other south west Australian systems and to Australian guidelines. However, there is no question that eutrophication has occurred post WWII given the increasing proliferation of Ruppia, its epiphytes and macroalgae.

  • Unlike the benthic vegetation, based on the historical data we have, there appears to be little change apparent in the water quality over time. This suggests that to date the Inlet is buffering the nutrient input effectively, presumably in the form of the Ruppia, its epiphytes and macroalgal growth.

  • Much of the nutrient that enters the Inlet from the catchment, and the great majority of what is exported to the ocean, is in forms that plants and algae are unable to readily utilise.

  • Much of the nutrient that enters the Inlet from the catchment that is in forms that plants and algae can utilise is taken up by Ruppia, its epiphytes and macroalgae before it is even measurable in the water column of the Inlet, let alone before it has a chance to be exported to the ocean.

  • Given that only a small proportion of the nutrients are available to plants and algae, that their concentrations are unaffected by bar opening and that these nutrients are rapidly assimilated into Ruppia, epiphytes and macroalgae, it is believed that catchment management practices that target these available nutrients will rapidly translate into reduced Ruppia biomass and possible reduced macroalgal biomass.

  • Major phytoplankton algal blooms to date have all been linked to a chain of events that is initiated by bar opening and proceeds through salinity stratification, deoxygenation and increases in sediment nutrient recycling.

  • Sediment bio-geochemical studies (to be published in Wilson Inlet report to the community number eight) have demonstrated that under the present incidence of deoxygenation the sediments may recycle 15 times as much bioavailable nitrogen and 4 times as much bioavailable phosphorus to the water column as the catchment. With more frequent deoxygenation events than present, these quantities could double with potentially disastrous results for the Inlet.

  • Sediment bio-geochemical studies (to be published in Wilson Inlet report to the community eight) have demonstrated that under the present incidence of deoxygenation the sediments remove 25 times as much bioavailable nitrogen and significantly more bioavailable phosphorus from the water column as is exported to the ocean. With more frequent deoxygenation events than present, these quantities could be drastically reduced with potentially disastrous results for the Inlet.

We believe that while the Inlet is presently processing the nutrients that enter it effectively it is in a precarious balance based on the vulnerability of sediment nutrient recycling processes to adverse oxygen conditions. Maintaining adequate bottom water dissolved oxygen concentrations, and hence sediment nutrient processing is a major key to maintaining the health of the Inlet.

Until nutrient losses from the catchment are reduced, maintenance of the Ruppia as a buffer for the catchment derived nutrients is important to prevent the proliferation of macroalgae and an increased incidence of phytoplankton blooms.


© Copyright 2007 All rights reserved