Best Practice

Marine Farm (Credit: Aquaculture New Zealand)

Some of the risks from aquaculture activities discussed in the previous sections can be minimised through good siting of farms and design, such as marine mammal interactions, adverse impacts on landscape and natural character and alterations of water flows. Other risks, such as those associated with marine biosecurity, can be managed through good on-farm practices. Water quality impacts and cumulative risks are harder to predict and are therefore best managed adaptively, by phasing development within initially precautionary principles. The table below provides guidance on the ways different impacts can be managed for impact mitigation.

General Aquaculture Activities

Effects

Best Practice Response

Transporting spat and machinery used on marine farms around the country can spread diseases and pests  

Good management, including careful washing and drying of equipment before transportation, should be adopted to prevent spread of disease and pests

Fixed structures used by the marine farm can attract biofouling species which can spread to the surrounding environment 

Fixed structures should be regularly cleaned to prevent the build-up of biofouling species

Copper from antifouling paints can build up on the seabed to toxic levels  

Marine farms should either manually defoul equipment or use paints which are free of copper

Alteration of the behaviour of marine mammals as a result of marine farms obstructing access to, or use of, feeding grounds and other areas of their habitat 

Marine farms should be carefully located in order to ensure that access by marine mammals to habitual feeding, haul out, migratory routes and other areas is not obstructed.

Marine farms should not be located in areas which are used by dolphins for cooperative hunting.

Potential for marine mammals to become caught in longline or finfish nets used on the marine farm

Marine farms should use the best available technology and best techniques to minimise the risk that marine mammals will become trapped in nets (such as adequate net tension, enclosing anti-predator nets at the bottom, eliminating food waste and reducing the mesh size of nets) 1747

Debris from poorly maintained farms can be a hazard to other water users and to marine fauna

All non-biodegradable waste material should be removed from the coastal marine area, and structures should be adequately maintained to ensure their integrity. Lines should be kept under tension (this reduces likelihood of nuisance for other users and reduces likelihood of marine mammal entanglement)

Degradation of landscape values and natural character of the area

Marine farms should be sited away from areas with outstanding landscape or outstanding natural character values

Marine farms should be sited away from areas where the visual effects of the farm could be significant on landscape or natural character values

Marine farms can pose a hazard to watercraft and navigation 

Marine farms should be adequately lit at night to ensure safety of navigation

Marine farms should not be located in areas which obstruct navigation or safe anchorage, such as shipping routes and popular recreational vessel routes and anchorages

Shellfish

Effects

Best Practice Response

Effects on water quality through excretion of faeces and alteration of naturally occurring currents

Marine farms should be designed to minimise effects on currents, should be sited in areas with adequate flushing, and should be stocked with lower densities as to allow reduced build-up of faeces in the area

Depletion of naturally occurring plankton leaving less available for wild species  

The effects of shellfish farming on the amount of plankton available should be carefully managed, including the cumulative effects of having more than one shellfish farm in the same area

Effects on light-sensitive marine flora as a result of shading by the farm structure  

Marine farms should be located away from areas where they can have negative impacts on seagrass and other light sensitive species such as seaweeds

Changes to the seabed through deposition of shell, shellfish and faeces

Marine farms should be sited in areas where benthic habitats are less sensitive to impacts such as areas with a muddy substrate rather than rocky or sandy areas 

Effects on wild species as a result of changes to their environment  

Marine farms should be located away from areas where they can have negative impacts on species or habitats with special conservation value or of ecological importance 

Changes to patterns in the current and natural flow of water as a result of farms, particularly oyster racks, causing sand build up under the farm  

Proposals for marine farms should be accompanied by an assessment of the hydrodynamic patterns at the subject site, with current speeds and directions, flushing times and water dispersion patterns and modelling of how this will be affected by the proposed farm. 

Marine farms should not be sited in poorly flushing areas.

Abandonment of marine farm sites and structures when farming ceases  

If marine farming activity ceases, all structures associated with its use should be removed and the site rehabilitated. The consent authority should require this as a condition of consent or require a bond or payment to cover the cost of removal by the local authority 

King Salmon and Indigenous Fish

Effects

Best Practice Response

Increased likelihood of disease from high density stocking rates for fish farming

Good husbandry, reducing stress and appropriate nutrition can all help prevent disease outbreaks

Fish should not be farmed at high intensity to minimise the likelihood of disease

There should be single age class fish farms

Farm spacing should be at least one kilometre within the same management plan and at least 2.5 kilometre if not within the same management plan

Regular checking of equipment

Depletion of fish stocks when farmed fish are fed wild-captured fish or feed pellets made from wild-captured fish 

Minimise the proportion of wild-captured fish used to provide protein and oils in fish feed

Use feed which maximizes the conversion rate between the amount of wild fish consumed and the amount of farm fish produced

Only use wild fish from sustainable capture fisheries

Deposition of faeces and uneaten food causing changes to the physical, chemical and biological nature of the seabed and water quality

High density stocking rates should be avoided, high quality feed used to reduce the amount required, and automated feeding systems deployed which stop dispensing when they detect uneaten food in the water 

Farms should be located in areas which flush well.

Adopt integrated co-culture/multi-trophic aquaculture where possible (where finfish, mussels, seaweed and other species are grown in an integrated farm where one species counteracts the negative effects of another)

Effects on local biodiversity as a result of changes to their environment  

Marine farms should be located away from areas where they can have negative impacts on species or habitats with special conservation value or ecological importance 

Escape of farmed fish and spread of diseases to wild fish

Fish farms should be designed to minimise escapees

Breeding of escaped fish with wild fish that adversely affects the genetic robustness of the wild population

All reasonable efforts should be made to prevent the escape of farmed fish, including utilising new technology where available 

Harm to the marine environment and to humans consuming the products from chemicals used to treat the fish 

Finfish should be farmed at a density which limits the likelihood of disease and therefore does not require the use of antibiotics and other theraputants, as has been the case up to this point in New Zealand

The aquaculture industry has developed Environmental Codes of Practice designed to promote the adoption of best industry practices, throughout the growing and harvesting cycles, in order to minimise potential effects on the environment. 1770  These Codes have been independently benchmarked against similar international standards. They are specific to three species:

  • Greenshell™ Mussel Industry Environmental Code of Practice, 1999 (Revised 2007)
  • Oyster Industry Code of Practice, 2007
  • Finfish Aquaculture Environmental Code of Practice, 2012

Aquaculture New Zealand is currently re-drafting the Environmental Codes of Practice in order to make sure that they reflect current industry practices, changes to the regulatory framework and the latest market conditions, as well as incorporate any new global standards. They are planning to set Key Performance Indicators for each Code. It is hoped that an online sustainability assessment and reporting tool can be prepared. This is intended for use by marine farm operators, third party auditors and the industry body to help rate and consequently improve environmental performance against the standards. One of the aims of this work is that individual operators can use the environmental management system as a pathway to become fully accredited with an international certification.

 

  1. Kemper C et al., 2003

  2. http://aquaculture.org.nz/environment/sustainability/

Last updated at 1:31PM on February 25, 2015