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Marine Produce Australia: Cone Bay Barramundi Aquaculture ...

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3. Environmental Objectives<br />

3.1 Best-practice marine farming<br />

Best practice environmental management depends on knowledge of the potential effects of<br />

sea-cage aquaculture together with an understanding of the host environment, including the<br />

extent and variety of benthic habitats (particularly BPPHs), the characteristic water quality<br />

and the extent of local biodiversity. Utilising this knowledge, proactive management<br />

strategies have been developed to maximise farming efficiency and to minimise the likelihood<br />

of adverse environmental impacts. Management strategies have been (and continue to be)<br />

developed by MPA through consultation with scientists, regulators and other marine farm<br />

operators. Further information on best practice marine farming can be read in the<br />

Department of Fisheries, Environmental Code of Practice for the Management of Western<br />

<strong>Australia</strong>’s <strong>Marine</strong> Finfish Industry, and The Scottish Executive (ASFA) 2003, which MPA has<br />

used as the basis for best practice marine farming.<br />

A key consideration in best practice marine farming is management of fish feeds, such that<br />

feed waste is minimised. The key proactive feed-wastage management strategies to be<br />

employed by the proponent are outlined below:<br />

� The company strategy is to minimise wasted feed through controlling overfeeding;<br />

� Stocking densities will be managed to maintain optimum biological stocking rates to<br />

promote fish health and growth, and to reduce the impact of fish and feed waste on the<br />

seabed in the immediate vicinity of each sea cage;<br />

� Fallowing practices will be used as required to facilitate restoration of sediment quality<br />

under the sea-cages so as to comply with the specified level of ecological protection;<br />

� Feed cameras and or pellet sensors will be used during fish feeding to determine optimum<br />

feed input rates and correct stop feeding signals, thereby reducing wasted feed; and<br />

� All farm fish mortalities will be removed from the sea-cages twice weekly.<br />

3.2 Best-practice environmental management<br />

The EMMP has been designed according to the framework developed by the National Water<br />

Quality Management Strategy (NWQMS): the Environmental Quality Management Framework<br />

(EQMF). The Government of Western <strong>Australia</strong>n has endorsed the state-wide implementation<br />

of the EQMF on a priority basis (Government of Western <strong>Australia</strong> 2003, 2004).<br />

Consistent with the NWQMS, the EMMP has adopted a structured approach to management.<br />

MPA has agreed to maintain the EVs and EQOs (see Table 1.1) through adherence to<br />

appropriate EQG and EQS. The EQG and EQS criteria have been set in the context of EQO1:<br />

Maintenance of Ecosystem Integrity. It is noted that risks posed by this aquaculture proposal<br />

are such that if the EQO for the EV Ecosystem Health is met, then all other EVs will also be<br />

protected.<br />

3.3 Environmental performance indicators/criteria<br />

EQG and EQS have been developed in the context of the Ecological Protection Zones specified<br />

in Schedule 1 of Ministerial Statement 798.<br />

Environmental Quality Guidelines (EQG): are threshold numerical values or narrative<br />

statements, that if met, indicate there is a high degree of certainty that the associated<br />

environmental quality objective has been achieved. If the guideline is not met, there is<br />

uncertainty as to whether the associated environmental quality objective has been achieved<br />

and a more detailed assessment against the EQS is triggered.<br />

Environmental Quality Standards (EQS): are threshold values or narrative statements<br />

that indicate a level beyond which there is a significant risk that the associated environmental<br />

quality objective has been not been achieved. The response would normally focus on<br />

identifying the cause (or source) of the exceedance and then reducing loads of the<br />

contaminant of concern (i.e. source control) and may also require in situ remedial work to be<br />

undertaken. EQS are generally equivalent to the water quality objectives described in<br />

ANZECC/ARMCANZ (2000).<br />

12 Oceanica: <strong>Marine</strong> <strong>Produce</strong> <strong>Australia</strong>: <strong>Cone</strong> <strong>Bay</strong> <strong>Barramundi</strong> <strong>Aquaculture</strong>, Environmental Monitoring & Management Plan

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