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Contaminant pathways in Port Curtis: Final report - OzCoasts

Contaminant pathways in Port Curtis: Final report - OzCoasts

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<strong>Contam<strong>in</strong>ant</strong> <strong>pathways</strong> <strong>in</strong> <strong>Port</strong> <strong>Curtis</strong>: F<strong>in</strong>al <strong>report</strong>Executive summary(i) Risk-based managementThe SLRA illustrated the utility of us<strong>in</strong>g a risk-based approach to contam<strong>in</strong>antmanagement. Ow<strong>in</strong>g to limited resources and more time-critical research priorities,the CRC was not able to assess the risks posed by many organic contam<strong>in</strong>ants.We recommend that this issue now be covered, but with a staged approach. TheCRC research has shown the value of us<strong>in</strong>g contam<strong>in</strong>ant bioaccumulation as an<strong>in</strong>dicator of ecosystem health. A first stage would therefore be the measurement oforganic contam<strong>in</strong>ants <strong>in</strong> <strong>in</strong>dicator organisms <strong>in</strong> <strong>Port</strong> <strong>Curtis</strong>. Further <strong>in</strong>vestigationsmay be necessary if bioaccumulated organic contam<strong>in</strong>ants prove to be significant.Mercury <strong>in</strong> piscivorous fish such as barramundi can be elevated ow<strong>in</strong>g to foodcha<strong>in</strong> biomagnification. This is an issue of regional importance and should not beforgotten given the large recreational and commercial fish<strong>in</strong>g <strong>in</strong>dustries present <strong>in</strong><strong>Port</strong> <strong>Curtis</strong> and surround<strong>in</strong>g regions. The characterisation of mercurybioaccumulation and biomagnification through food webs over the coastal regionof the whole Central Queensland region is appropriate.(ii) Improved monitor<strong>in</strong>gThe <strong>Contam<strong>in</strong>ant</strong> Pathways study and the SLRA have shown the value of ‘goodquality data’. It is recommended that future monitor<strong>in</strong>g adopt and enforce rigorousquality assurance protocols to ensure quality is ma<strong>in</strong>ta<strong>in</strong>ed.As noted earlier, contam<strong>in</strong>ant concentrations may fluctuate over various timescales <strong>in</strong> <strong>Port</strong> <strong>Curtis</strong>. Such variations are not easily discerned with a discretesampl<strong>in</strong>g approach. Time-<strong>in</strong>tegrated monitor<strong>in</strong>g such as biomonitor<strong>in</strong>g us<strong>in</strong>gdeployed organisms (e.g. oysters) and chemical surrogates such as diffusivegradients <strong>in</strong> th<strong>in</strong> films (DGT) for metals and solvent-filled dialysis cells for organics(passive samplers) is therefore recommended. Seasonal monitor<strong>in</strong>g may also beconsidered to determ<strong>in</strong>e if there are any seasonal fluctuations to contam<strong>in</strong>antloads <strong>in</strong> <strong>Port</strong> <strong>Curtis</strong>.(iii) Ability to predict contam<strong>in</strong>ant concentrations and effectsA key tool <strong>in</strong> susta<strong>in</strong>able management is the ability to predict impacts. Werecommend that the further development of the hydrodynamic model <strong>in</strong>conjunction with contam<strong>in</strong>ant data and a subsequent suite of predictive models ispursued. The model should be expanded to <strong>in</strong>clude The Narrows region and someof the major estuaries <strong>in</strong> <strong>Port</strong> <strong>Curtis</strong> to assist <strong>in</strong> understand<strong>in</strong>g the contribution ofmetal load from po<strong>in</strong>t sources, and flows from the Fitzroy River to <strong>Port</strong> <strong>Curtis</strong>.Predictive models of metal bioaccumulation and biological impact (or establish<strong>in</strong>gif environmental harm has occurred) are also worthy of consideration. The effect ofx

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