2.7 Proposal to expand marine farming in Macquarie Harbour referred to the Minister
34 On 29 May 2012, DPIPWE referred the proposed expansion of marine farming activity in Macquarie Harbour to the Minister for determination pursuant to the EPBC Act. The referral, together with 12 appendices, is at pp 2-354 of Ex A1.
35 A "short description" of the proposed action is set out at p 6 of Ex A1:
The proposed action is:
• The expansion of marine farming operations, that will occur consistent with the 2012 amendment to the Macquarie Harbour Marine Farming Development Plan, which will include the following activities:
• The arrangement and securing of sea pens for fish farming;
• The construction of associated water based infrastructure;
• The operation of fish farms including:
• Servicing and maintenance of sea pens and associated water and land based infrastructure;
• Feeding and managing the health, waste, processing and predators of fish in the farms;
• Transportation of fish to and from the farms across water and land.
(Footnote omitted.)
36 The referral provided a more detailed description of the proposed action (Ex A1 pp 11-20):
Background - Expansion of Marine Farming
The approval of the amendment to the MFDP has paved the way for the following to occur:
• change in location of existing marine farming zones and lease areas
• increase in leasable area within zones
• addition of a new zone
• changes to management controls/operations which apply to zones
Changes to Lease Areas and Locations
To progress expansion of salmonid farming activities in Macquarie Harbour the Marine Farming Planning Act 1995 required an amendment to the existing Macquarie Harbour Marine Farming Development Plan October 2005. A full description of the amendment as it was initially proposed can be seen in Appendix 2 with the final amendment provided in Appendix 3. The marine farming review panel (MFRP) recommended further modifications to management controls post public consultation which, whilst not changing the intent of the management controls proposed in Appendix 2, did clarify wording around a number of issues.
The area covered by the Macquarie Harbour Marine Farming Development Plan October 2005 (DPIPWE 2005) is the physical extent of the harbour outside of the Tasmanian Wilderness World Heritage Area (TWWHA) and consists of all that area bounded by the high water mark between a line drawn from Coal Head and Steadmans Point across the harbour to the south east (being the Western Boundary of the TWWHA) and the entrance to the harbour to the west at a line drawn between Braddon Point through Bonnet Island Light to the western shore. …
The Act provides for the preparation of MFDPs that designate areas of State waters as marine farming zones and the maximum area that may be used for marine farming operations within zones. The Act also provides for provisions for operational constraints on marine farming activities.
The Macquarie Harbour MFDP prescribes 10 marine farming zones within the plan area which provide for the culture of salmonids in 564 hectares of marine farming lease area.
The amendment to the Macquarie Harbour MFDP has resulted in moving some zones to areas better suited to salmonid culture and expanding the maximum leasable area by 362 hectares to 926 hectares - this expansion includes the addition of a farming zone.
Variations to zone locations and sizes (including maximum leasable areas) has taken effect with the approval of the amendment, however new lease areas and variations to existing leases (including sizes and locations) will need to be approved consistent with the amendment. It is the intention of industry and the Planning Authority that these steps occur within quick succession. The specific changes to each zone are discussed in Appendix 1. … Table 2.1 indicates changes to locations and leasable areas.
Three separate companies have been working jointly on the proposed expansion of salmonid farming activities in Macquarie Harbour. These include Tassal Operations Pty Ltd (Tassal), Huon Aquaculture Group Pty Ltd (Huon) and Petuna Aquaculture Pty Ltd (Petuna), all three of which have existing salmonid farming operations within the MFDP area as it existed prior to the 2012 Amendment. It is expected that these companies will take up the expanded lease area. …
Changes to Management Controls
Section 3 of the Macquarie Harbour Marine Farming Development Plan October 2005 contains management controls to manage and mitigate negative effects that marine farm operations may have within the plan area.
The MFDP as amended has a number of existing management controls that will remain unchanged. Eleven new management controls have been inserted and 5 controls have been amended to cater for the proposed expansion. Appendix 3 illustrates the revised management controls and Appendix 4 provides context around new versus amended controls.
The Proposed Action
The proposed action is:
• the expansion of marine farming operations, that will occur consistent with the 2012 amendment to the Macquarie Harbour Marine Farming Development Plan, including the following activities:
• The arrangement and securing of sea pens for fish farming;
• The construction of associated water based infrastructure;
• The operation of fish farms including:
• Servicing and maintenance of sea pens and associated water and land based infrastructure;
• Feeding and managing the health, waste, processing and predators of fish in the farms;
• Transportation of fish to and from the farms across water and land.
The following components of each aspect of the action are described below, with specific details on activities to occur within each marine farming zone provided in Appendix 1 and Appendix 2:
Salmon Farming Operations Consistent with the MFDP
• Construction and Infrastructure Development
• Mooring and Grid System
• Size and Configuration of Sea Pens
• Other Infrastructure/Construction
• Operation of fish farms
• Servicing and Maintenance of Sea Pens and Associated Infrastructure
• Boat Movements
• Infrastructure Maintenance
• Feeding and Managing Health, Waste, Processing and Predators of fish in the Farms
• Fish size/stocking density
• Fish Health
• Predator Control
• Waste Management
• Environmental Management
• Transportation of fish to and from the farms across water and land
Salmonid Farming Operations Consistent with the MFDP
The expansion of salmon farming operations within Macquarie Harbour, consistent with the 2012 Amendment of the MFDP will include activities associated with the construction of aquatic components of marine farms and ongoing operation of both terrestrial and aquatic components of marine farms. These include:
• The construction, arrangement and securing of sea pens for fish farming;
• The construction of associated land and water based infrastructure;
• The operation of fish farms including:
• Servicing and maintenance of sea pens and associated water and existing land based infrastructure;
• Feeding and managing the health, waste, processing and predators of fish in the farms;
• Transportation of fish to and from the farms across water and land.
Construction and Infrastructure Development
In order to operate, the expansion of fish farms in Macquarie Harbour requires the construction and placement of new and existing infrastructure.
New mooring and grid structures are required to moor existing, and additional sea pens to. The size of these pens varies across leases, as does their configuration and locations. Additional on water structures are also required for servicing expanded farms (e.g. barges).
Mooring and Grid system
Each company will use their own mooring system to attached sea pens/cages to. There are currently approximately 132 cages in Macquarie Harbour across 5 leases. Planned expansion of the industry under the amendment to the MFDP will see an increase in cage numbers to approximately 211. The mooring systems to be used across zones are described in Appendices 1 and 2. Baseline surveys which establish whether there will be any impacts from mooring and grid systems are not part of this action.
Size and configuration of Sea Pens
The location and configuration of pens associated with the amendment of the MFDP for each company are described in Appendices 1 and 2. … There are no change[s] to Zones 7 and 8 as a result of this proposal.
Other Infrastructure/Construction Aspects
Additional land and water based infrastructure will be required in order to operate fish farms associated with the proposed expansion. There is likely to be a need for some improvements to land based facilities over time.
Huon aquaculture immediately require a new centralised feeding system barge, with a view to a centralised feeding system involving dedicated feed barges proposed for each zone into the future. Additional power generators will be associated with new barges.
Two additional feeding boats are also likely to be required in the next 7 years.
Tassal's feed storage shed is inadequate to cater for current needs and is in a poor state of repair - in addition access to the site is restricted (Appendix 2).
It is estimated that traffic movements will increase from around 90 to a maximum of 228 within 5 years - to manage this impost on Strahan township, and to streamline operations an aquaculture hub away from the Strahan township has been proposed.
Operation of Fish Farms
The operation of fish farms in Macquarie Harbour requires a range of activities within the key areas listed below:
• Servicing and maintenance of sea pens and associated water and land based infrastructure;
• Feeding and managing the health, waste, processing and predators of fish in the farms;
• Transportation of fish to and from the farms across water and land.
Servicing and Maintenance of Sea Pens and Associated Infrastructure
Servicing of on water infrastructure involves the movement by boat of maintenance teams multiple times a day to sea pens to undertake a range of maintenance (and stock husbandry) tasks. Boat movements and maintenance tasks are described in detail below.
Boat Movements
Boat movements associated with marine farming activities in Macquarie Harbor can be placed into two categories; vessel movements from shore based operations to marine based operations and vessel movements within lease areas. Table 2.2 illustrates current and proposed boat movements by type.
Vessel movements from shore based operations to marine based operations consist of staff transfers to lease areas, feed transfer, net and equipment transfer, dive team movements and harvest vessels (Table 2.2). The proposed increase in movements represents an increase from 59 movements to 158 movements per week. Table 2.2 does not include movements undertaken by smaller vessels within lease areas.
Companies in Macquarie Harbour usually moor a number of vessels within the lease areas which are used to service the lease during operational hours. These vessels generally do not leave the lease area but travel between cages and mother barges.
* Tassal uses two existing marine farming leases in Macquarie Harbour which will be serviced by the same vessels on the one trip, therefore the traffic from Strahan to the leases will not change considerably but the distance travelled by the vessels will increase.
It should also be noted that harvesting will not occur all year round and from the same lease each year, for example, Tassal will harvested for 6 months of the year from Zone 9 every second year. The figures above have included harvest vessel movements all year round. Appendix 1 contains detailed descriptions of boat movements by zone.
Infrastructure Maintenance
A variety of maintenance tasks are undertaken either routinely or for a specific purpose. These tasks include:
• Checking of cage nets via scuba diving
• Inspection of bird nets
• Repair of nets
• Vessel maintenance for barges
• Routine generator and other equipment maintenance
• Inspection of moorings (divers and ROV)
Off water infrastructure maintenance, including maintenance on large barges occurs either at land based sites or in specialised workshop environments in Devonport and Burnie. Boat servicing, outboard servicing etc occurs at the slip yard in Strahan. Net maintenance and construction occur at land based net areas.
Specific maintenance activities are described by zone in Appendix 1. There will be no change to activities occurring at Zone 7 and Zone 8.
Feeding and managing the health, waste, processing and predators of fish in the farms
The management of fish farming activities includes the management of:
• fish size and stocking densities;
• fish feeding;
• fish health;
• predator control;
• waste management;
• environmental management.
Fish Size/Stocking Density
It is the intention that two species will be cultivated in the expanded marine farming operations in Macquarie Harbour: rainbow trout (Oncorhynchus mykiss) and atlantic salmon (Salmo salar).
Sites would be stocked with intake fish ranging in size from 80g - 300g depending on species and company. Harvest size would range from over 4kg to 5kg.
Current estimates are that around 3.2 million smolt are used in the harbour per year - this figure is expected to increase to around 6.3 million smolt with the expansion.
The maximum stocking density of fish would increase from 15 kg/m³ to 17 kg/m³ of cage volume.
Species and stocking approaches by zone can be seen in Appendix 1.
Information regarding fish size and number, stocking density (also biomass limits on an area basis i.e. tonnes/ha) and feed volume all have links to the modelling used to determine the sustainable carrying capacity (total biomass and stocking density) of Macquarie Harbour for this development. They are also associated with the adaptive management framework that is proposed. Of these, the potential to prescribe stocking density and biomass limits have been incorporated into management controls.
Fish Feeding
Feeding is currently undertaken via boats using water cannons as well as by centralised feed systems with the operator either using camera feedback systems to control the feeding or, the system responding to appetite ingestion rate of the fish to feed to satiation without waste.
The feed used is commercial extruded feed and dry extruded sinking pellets sourced from both within Tasmania and interstate. There is no change to the types of feed to be used in the expansion from currently farmed area. The volumes of feed will vary depending on market expansion, smolt type, smolt size, transfer date, photoperiod regime, water temperature, fish health, and harvest profile.
Sediment monitoring is carried out during the Annual Video Surveys as required by marine farming licence conditions, as well as during routine internal environmental monitoring programs companies run. Monitoring methods follow those employed to assess seafloor condition as outlined in the Monitoring Protocols of the Fish farm licences.
Details of each company's approach can be seen in Appendix 1.
Fish Health
Currently, there are no serious disease issues in Macquarie Harbour. Previously, a number of diseases have been identified in Macquarie Harbour; these have included yersiniosis, marine aeromonad disease of salmonoids (MAS) and vibriosis. In 2006, Ichthyophonus caused mortality in rainbow trout. In addition, Aquabirnavirus, Reovirus and a rickettsia-like organism (RLO) have also been detected.
The key component in the preventative disease program for Macquarie Harbour is vaccination against Marine Aeromonad Disease and vibriosis. Since the introduction of the vaccination process, there have been no outbreaks of these diseases. Additionally, there is mandatory health surveillance carried out by Department of Primary Industries, Parks, Water and Environment (DPIPWE) personnel within the framework of the Tasmanian Salmonid Health Surveillance Program (Tas SHSP) which is a joint Industry and Government Program.
Further, the current operators within the plan area have developed a Fish Health Management Plan (FHMP) which will provide a specific detailed strategy for the ongoing management of fish health in Macquarie Harbour (See Appendix 2). The operators have signed off on the strategies outlined in the FHMP which consists of a combination of compliance, best practice and regulation through management controls and marine farming licence conditions. The FHMP addresses detailed, standard operating practices to prevent disease from entering the harbour, to prevent spread and impact of disease in the harbour and to respond to emergency disease situations. The FHMP will be reviewed annually or more frequently if needed.
Under expanded operations there will be an associated increase in the real amount of vaccinations being administered to smolt - currently trout and salmon have one vaccination by injection and one by bath in the hatchery and this will continue.
Chemical Usage
Chemical use in the marine environment will be restricted to fuels and oil based lubricants associated with boats, and disinfectants, cleaning agents and antibiotics. Fuels would constitute by far the majority, by volume, of the total amount of chemicals proposed to be used. Small volumes of disinfectants are used in a variety of manners for hygiene purposes, and cleaning agents are used on harvest infrastructure following harvesting operations. Antibiotics would only be prescribed over short periods to address illness and animal welfare issues. It is not possible to forecast antibiotic use, but it is expected that antibiotic use will remain low, if not absent, due to improved husbandry practices and effective vaccines.
It is proposed that most chemical usage will continue across the expansion area proportional to the increase in biomass being farmed. Based on this, it is predicted that a 263% increase will occur in the chemical use associated with the expansion.
Predator Control
Australian and New Zealand Fur Seals are a potential predator of salmon and trout in marine farms. The main means of controlling seal predation will be via exclusion, by means of heavily weighted sinker ring and tensioned cage nets and above water predator nets. Net barriers may also be required above the handrails to prevent seals from jumping into the cages. There is ongoing investigation and trialling of new exclusion and deterrent technologies. Under the DPIPWE's seal management protocols, marine farmers can apply to the Department to relocate problem seals.
Birds are also a potential problem. The means of control to be used is prevention of access to the fish or to feed pellets, by means of properly designed and supported bird nets. See Appendix 1 for further zone specific details.
Waste Management
Both solid and liquid wastes are produced by marine farms and are managed by different means. It is expected that there will be a net increase in most waste streams generated commensurate with an increase in stocked cage numbers. Whilst this will not be realised during the first year of the expansion, there will be a gradual staged increase over time until all sites are fully stocked, at which point a 62% increase from current levels of land-based disposal of waste will be realised. Fish mortality wastes are expected to increase by 60% from current levels (see below).
Solid wastes include fish bodies (mortalities), waste from the harvesting process (including body parts and bloodwater), wastes on nets and uneaten feed.
Mortalities are collected and buried at an approved mort lease site or mort pit. Bloodwater and solid waste from the harvest process is contained in harvest bins during the harvest and either delivered to a processing facility at Devonport or, the waste is separated with the solid component going to mort pits, and the liquid component released in to the municipal sewerage scheme through a Trade Waste Agreement with Cradle Mountain Water Authority depending on the marine farming company (Appendix 1).
Current levels of fish mortalities across the industry in Macquarie Harbour are generally around 1.97% (approx 63000 fish) of stocked numbers by live weight. It is expected that this rate would remain comparable following the expansion resulting in approx 124000 dead fish at full production. This would be an increase from current totals of around 60%.
Local government approval is required for fish waste volumes 250µM at a depth of 3cm within a core sample.
Biological:
• A 20 times increase in the total abundance of any individual taxonomic family relative to reference sites.
• An increase at any compliance site of greater than 50 times the total Annelid abundance at reference sites.
• A reduction in the number of families by 50 per cent or more relative to reference sites complete absence of fauna.
There must be no significant impacts within the Lease Area. The following impacts may be regarded as significant:
Visual impacts within Lease Area:
• Excessive feed dumping.
• Extensive bacterial mats (e.g. Beggiatoa spp.) on the sediment surface prior to restocking.
• Spontaneous gas bubbling from the sediment.
lf a significant impact (as defined in the licence conditions and outlined above) is detected within or outside the lease areas, during annual compliance monitoring surveys, targeted management responses are required, in addition to possible further investigation and depositional modelling.
Targeted management responses are implemented by way of management controls outlined in the Macquarie Harbour Marine Farming Development Plan as amended, by the Secretary of the Department of Primary Industries, Parks, Water and Environment and involve one or more of the following actions:
• reduction in biomass,
• reduction in nitrogen output, or
• redistribution of biomass.
These management controls ore designed to regulate the stressor, both soluble and particulate, loads. Given that organic enrichment effects are lease specific, direction by the Secretary to reduce input is primarily focused on reducing biomass load, or redistributing biomass load within a specific marine farming lease area, including fallowing a particular pen bay or pen bays.
Where a significant impact, as defined, is observed, and specific management actions are required by the Secretary to be implemented, the leaseholder is required to undertake a follow-up benthic video assessment to m on it or benthic recovery.
The regulation of benthic impact from marine farming operations, as described above, has been in place for all marine farming operations in Tasmanian waters for the last 16 years. During this period it has been demonstrated that organic loading effect s from farming operations can be effectively managed using the environmental management framework outline above. This, together with the information regarding the distribution of Maugean Skate within Macquarie Harbour, including in close proximity to existing marine farm operations, leads the Department to the view that the expansion of marine farming activities in Macquarie Harbour will not have a significant impact on the MNES - Maugean Skate.
Tasmanian Wilderness World Heritage Area and Maugean Skate
Issues associated with water quality have the potential to impact on two MNES - the Tasmanian Wilderness World Heritage Area and the Maugean Skate. The Department has worked closely with representatives of the three companies who will be undertaking the marine farming expansion activities to develop an appropriate water quality monitoring program and water quality limits to ensure that the proposed expanded marine farming activities do not have a significant impact on these matters of MNES.
As you are aware, as part of the ongoing development of the model which was used by the State Government to assess the amendment to the Macquarie Harbour Marine Farming Development Plan, the three companies have been collecting monthly water quality data since September 2011. The model will be recalibrated during the first review cycle of the adaptive management framework, using at least 12 months of water quality data within the harbour that reflects the current extent of marine farming activities.
Marine farming licences will contain conditions that require the licence holders to undertake a water quality program to monitor changes in indicator levels relative to prescribed limits within Macquarie Harbour.
The monitoring program will involve continued assessment of the water quality indicators - ammonia, nitrate and dissolved oxygen, at 11 sites throughout the Harbour (refer Map 2 for sample locations) until mid 2013 after which the number of monitoring sites will be reviewed. In addition the marine farming licences will require quarterly reporting and interpretation of the results of the water quality monitoring program.
Water quality limits will be contained within marine farming licences, and will be based on the 80th/20th percentile values of the water quality indicators, based on the predictive biogeochemical and hydrological model outputs. The percentage values of the water quality indicators will be:
• Ammonia - 80th percentile;
• Nitrate - 80th percentile;
• Oxygen - 20th percentile.
As a precautionary measure to ensure that expansion of salmonid production in the harbour does not significantly impact on water quality, interim water quality limits have been established for the above water quality indicators. These interim limits will be in place until the first review of the adaptive management framework is completed in mid 2013, and will be included as mandatory conditions within the marine farming licences.
In mid 2013 the interim water quality limit levels will be reviewed. The approach to water quality limits after the review will be based on the 80th/20th percentile as is the case for the interim levels outlined above. The reviewed figures will be derived from a recalibrated biogeochemical and hydrological model that will be informed, amongst other things, by at least 12 months of water quality data collected from the harbour, and further predictive modelling.
The interim water quality limits and the water quality monitoring requirements contained within marine farming licences will not be updated, and additional finfish biomass above and beyond that indicated in the Secretary's letter of 27 June 2012 will not be able to be added to the harbour until such time as the review is completed, and the marine farming licence conditions amended to reflect the outcome of the review.
The environmental condition of Macquarie Harbour has undergone a number of assessments, and in each of those assessments it has been determined that the harbour is not pristine, and has had some level of impact from past activities.
For example the Australian Natural Resource Atlas describes Macquarie Harbour as being of modified condition, and under the Conservation Significance of Tasmanian Estuaries project of my Department the harbour is classified as having low conservation significance as a result of being moderately degraded. (See Attachment 2 for further information).
In addition, if the ANZECC Classifications and Recommendations framework is used Macquarie Harbour would be described as a slightly to moderately disturbed ecosystem in which biological diversity may have been adversely affected to a relatively small but measurable degree by human activity.
The ANZECC Guidelines 2000 recommended that guidelines be developed on the basis of biological effects data, where such data is not available, or alternatively use base guidelines on the 80th and/or 20th percentiles of data from reference sites. In particular for slightly to moderately disturbed ecosystems such as Macquarie Harbour it is recommended that:
The trigger values are derived from the 80th and/or 20th percentile values obtained from an appropriate reference system. For stressors that cause problems at high concentrations (eg. nutrients, salinity), that the 80th percentile of the reference distribution as the low-risk trigger value. For stressors that cause problems at low levels (eg. low dissolved oxygen in waterbodies), use the 20th percentile of the reference distribution as a low-risk trigger value.
Biogeochemical and hydrological modelling has been used to consider the effects on water quality arising from the expanded salmonid farming activities. The modelling has predicted that certain parameters will be elevated with increased production. Assessment of the effects of the modelled outputs predicts that at the maximum level of modelled production there will be no significant impact on the environment and ecosystems of Macquarie Harbour, and that the expected effects fall within an 'acceptable' level of change.
The predictive biogeochemical and hydrological model output has been adopted for use for establishing the values of the water quality indicators because it is a specific tool that has been developed for Macquarie Harbour, taking account of the existing knowledge as it relates to the hydrodynamics of the harbour, and the existing environmental conditions, rather than applying a generic set of environmental guidelines. The model defines the limits of predicted change within acceptable ecological and toxicological levels as discussed in relevant literature and environmental guidelines. As such, the model will be used as the reference system when setting the water quality limits.
The interim limit levels for each of the water quality indicators are as follows:
Indicator Limit
Ammonia (at 2 metres) 0.033 mg/L
Ammonia (at 20 metres) 0.024 mg/L
Nitrate (at 2 metres) 0.053 mg/L
Oxygen (at 2 metres) 6.82 mg/L