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Monitoring environmental impact of fish cages in the Mediterranean.
The MERAMED project (funded by the EU) undertook a screening cruise in July
2001 where 7 marine fish cage farms in Greece were surveyed to test Scottish and
Norwegian environmental monitoring techniques (Figure 1). These farms covered a
wide variety of cage site types, depth and annual production in order to ensure that the
methodology and modelling that is being developed under the research project is
suitable for all types of fish cage farms found in the Eastern Mediterranean.
Surveys were undertaken at 7 cage farms in the Aegean and Ionian seas by the
research vessel Philia (Figure 2) belonging to the Institute of Marine Biology Crete.
Sites covered the full range of locations at different depths, at varying degrees of
exposure to wave action, over different types of seabed at different production levels,
farmed species and feeding practices.
Figure 2. Research vessel Philia, Institute of Marine Biology Crete
Figure 1. Surveying a Greek cage farm
A range of survey methods and equipment was tested based on what is presently used
in Norway, Scotland and Greece. This included current meters, conductivity,
temperature and oxygen profiles through the water column (CTDO) (Figure 3),
Sediment Profile Imaging (SPI) (Figure 4), video/underwater photography using a
remotely operated vehicle (ROV) (Figure 5.), wind speed and direction
measurements, bathymetry (Rox Ann), drifting buoy survey (drogues), macrofauna
sampling, meiofauna sampling and sediment chemistry. At the same time methods
were developed to try and measure the biomass of wild fish close to the cages and
assess their effect on the quantity of suspended solids reaching the sediments below
the cages.
Figure 5. ROV remotely operated
vehicle
Figure 4. SPI Sediment Profile
Imaging
Figure 3. CTDO
This data was then linked to production data at the time of the survey to develop
mathematical models to predict the impact of cage farms on the sediments below the
cages under different conditions. The farmers received individual survey results with
recommendations on ways to mitigate impact.
A second more detailed cruise was undertaken at 3 of the original Aegean sites in
March this year. The objective of this cruise was to validate modelling predictions
with real data. One of the other main aims was to carry out a cost benefit comparison
study of survey methods and equipment.
During the second cruise, scientists also analysed the water column and sediments in
more detail, to identify geo-chemical and faunal changes in the sediments with
increasing distance from the fish cages. Data on fish production, food type and
feeding rates was collected from the fish farmers.
The third and final cruise took place in October this year. The scientists again visited
the same 3 sites and repeated all tasks in order to collect data after the summer season
when the highest feeding rate takes place and the cages have the highest biomass
before fish are sold. This is the official end of the research fieldwork although some
of the wild fish assessment work will continue through 2003.
The Project aims to develop survey methods that can be undertaken by the fish
farmer, independent surveyors and regulators depending on the site and potential
environmental impact of the farm. Therefore a comparative analysis of the different
survey methods was undertaken in order to propose a three-tier monitoring strategy.
At each tier, accuracy, sensitivity and cost (time, equipment, and personnel training
level) were evaluated for detecting the environmental effects of fish farming.
A summary of the approach and the corresponding activities at each level were tested
in the surveys are presented in the table below.
Simple/cheap àà Extensive/expensive
Activity Visual or descriptive Semi-quantitative Quantitative
Undertaken by: Local diver plus farm
boat
Farmer with some
specialized equipment or
small consultancy company
Research institute with
specialized boat or
large consultancy
company
Bathymetry Sea chart Echo sounder Rox Ann
Site
Characterization
Diver with photos Remotely Operated Vehicle Sediment Profile
Imaging
Benthic/sediment
samples
Small grabs Large grabs Corer
Sediment
condition
Colour, smell, presence
of Beggiatoa
Grain size, Total Organic
Carbon
Full chemical analysis
Benthic fauna Visual indicator species Semi-quantitative analysis Quantitative
Wild fish
community
Presence of indicator
species
Partial census Quantitative census
Wild fish are more abundant around the cages in the Mediterranean than the North
Atlantic. Therefore research is assessing the affects of the more plentiful wild fish on
the fate of the solid wastes (uneaten feed and faeces) and on the interactions between
farmed and wild fish, focusing on farm effluent flux and biodiversity.
For estimating the abundance and size of wild fish around the fish cages (Figure 6) a
visual census method was used, based on a digital stereo-video system and a software
package for photogrammetric analyses. Sediment traps and feed pellets marked with a
small amount of an indigestible food colour were used to trace the flux and dispersion
of particulate wastes around cages (Figure 7). Stomach samples of wild fish were
taken to identify fish species feeding on waste food or faeces. Feed pellets were
released on the sea-floor below fish farms and the food consumption by wild fish was
documented photographically (Figure 8). In addition, attempts are being made to
identify potential indicator species that will act as eco-indicators that can characterize
the impact of aquaculture activities on the fish community.
The initial results of the research will be ready by the end of 2003 and this will
provide guidelines and recommended monitoring methods for fish cages in the
Mediterranean. It is hoped that a training course will be conducted in May 2003 to
Figure 6. Mullets underneath a fish cage
Figure 7. Sealed sediment trap on the sea-floor
Figure 8. Wild fish (Spicara maena)
consuming feed pellets (3.5 and 5 mm
diameter) scattered inside a metal frame.
Circles mark counted pellets.
train fish farmers and other technicians in the methods and techniques developed from
the research. In addition a web based training module will be developed in the major
languages of the Eastern Mediterranean.
MERAMED is an EU funded research project. The full title is ‘Development of
monitoring guidelines and modelling tools for environmental effects from
Mediterranean aquaculture’. The aims of the research are to investigate and develop
scientifically validated methods for monitoring marine fish cage farms in the Eastern
Mediterranean and the main survey work is being undertaken in Greece.
The research is carried out by 5 partners, Akvaplan-niva AS, Norway, Seas Ltd.,
Scotland, Institute of Marine Biology of Crete, Greece, Dunstaffnage Marine
Laboratory, Scotland, and Institute of Marine Research of Kiel, Germany. Akvaplan-
niva are coordinating the programme, from its offices in both Tromsø Norway and
Athens.
Further information about the project and partners can be found at the web site at
www.meramed.com

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Better practice guidelines for fish farmers
 

Meramed article 2002

  • 1. Monitoring environmental impact of fish cages in the Mediterranean. The MERAMED project (funded by the EU) undertook a screening cruise in July 2001 where 7 marine fish cage farms in Greece were surveyed to test Scottish and Norwegian environmental monitoring techniques (Figure 1). These farms covered a wide variety of cage site types, depth and annual production in order to ensure that the methodology and modelling that is being developed under the research project is suitable for all types of fish cage farms found in the Eastern Mediterranean. Surveys were undertaken at 7 cage farms in the Aegean and Ionian seas by the research vessel Philia (Figure 2) belonging to the Institute of Marine Biology Crete. Sites covered the full range of locations at different depths, at varying degrees of exposure to wave action, over different types of seabed at different production levels, farmed species and feeding practices. Figure 2. Research vessel Philia, Institute of Marine Biology Crete Figure 1. Surveying a Greek cage farm
  • 2. A range of survey methods and equipment was tested based on what is presently used in Norway, Scotland and Greece. This included current meters, conductivity, temperature and oxygen profiles through the water column (CTDO) (Figure 3), Sediment Profile Imaging (SPI) (Figure 4), video/underwater photography using a remotely operated vehicle (ROV) (Figure 5.), wind speed and direction measurements, bathymetry (Rox Ann), drifting buoy survey (drogues), macrofauna sampling, meiofauna sampling and sediment chemistry. At the same time methods were developed to try and measure the biomass of wild fish close to the cages and assess their effect on the quantity of suspended solids reaching the sediments below the cages. Figure 5. ROV remotely operated vehicle Figure 4. SPI Sediment Profile Imaging Figure 3. CTDO
  • 3. This data was then linked to production data at the time of the survey to develop mathematical models to predict the impact of cage farms on the sediments below the cages under different conditions. The farmers received individual survey results with recommendations on ways to mitigate impact. A second more detailed cruise was undertaken at 3 of the original Aegean sites in March this year. The objective of this cruise was to validate modelling predictions with real data. One of the other main aims was to carry out a cost benefit comparison study of survey methods and equipment. During the second cruise, scientists also analysed the water column and sediments in more detail, to identify geo-chemical and faunal changes in the sediments with increasing distance from the fish cages. Data on fish production, food type and feeding rates was collected from the fish farmers. The third and final cruise took place in October this year. The scientists again visited the same 3 sites and repeated all tasks in order to collect data after the summer season when the highest feeding rate takes place and the cages have the highest biomass before fish are sold. This is the official end of the research fieldwork although some of the wild fish assessment work will continue through 2003. The Project aims to develop survey methods that can be undertaken by the fish farmer, independent surveyors and regulators depending on the site and potential environmental impact of the farm. Therefore a comparative analysis of the different survey methods was undertaken in order to propose a three-tier monitoring strategy. At each tier, accuracy, sensitivity and cost (time, equipment, and personnel training level) were evaluated for detecting the environmental effects of fish farming. A summary of the approach and the corresponding activities at each level were tested in the surveys are presented in the table below. Simple/cheap àà Extensive/expensive Activity Visual or descriptive Semi-quantitative Quantitative Undertaken by: Local diver plus farm boat Farmer with some specialized equipment or small consultancy company Research institute with specialized boat or large consultancy company Bathymetry Sea chart Echo sounder Rox Ann Site Characterization Diver with photos Remotely Operated Vehicle Sediment Profile Imaging Benthic/sediment samples Small grabs Large grabs Corer Sediment condition Colour, smell, presence of Beggiatoa Grain size, Total Organic Carbon Full chemical analysis Benthic fauna Visual indicator species Semi-quantitative analysis Quantitative Wild fish community Presence of indicator species Partial census Quantitative census Wild fish are more abundant around the cages in the Mediterranean than the North Atlantic. Therefore research is assessing the affects of the more plentiful wild fish on the fate of the solid wastes (uneaten feed and faeces) and on the interactions between farmed and wild fish, focusing on farm effluent flux and biodiversity.
  • 4. For estimating the abundance and size of wild fish around the fish cages (Figure 6) a visual census method was used, based on a digital stereo-video system and a software package for photogrammetric analyses. Sediment traps and feed pellets marked with a small amount of an indigestible food colour were used to trace the flux and dispersion of particulate wastes around cages (Figure 7). Stomach samples of wild fish were taken to identify fish species feeding on waste food or faeces. Feed pellets were released on the sea-floor below fish farms and the food consumption by wild fish was documented photographically (Figure 8). In addition, attempts are being made to identify potential indicator species that will act as eco-indicators that can characterize the impact of aquaculture activities on the fish community. The initial results of the research will be ready by the end of 2003 and this will provide guidelines and recommended monitoring methods for fish cages in the Mediterranean. It is hoped that a training course will be conducted in May 2003 to Figure 6. Mullets underneath a fish cage Figure 7. Sealed sediment trap on the sea-floor Figure 8. Wild fish (Spicara maena) consuming feed pellets (3.5 and 5 mm diameter) scattered inside a metal frame. Circles mark counted pellets.
  • 5. train fish farmers and other technicians in the methods and techniques developed from the research. In addition a web based training module will be developed in the major languages of the Eastern Mediterranean. MERAMED is an EU funded research project. The full title is ‘Development of monitoring guidelines and modelling tools for environmental effects from Mediterranean aquaculture’. The aims of the research are to investigate and develop scientifically validated methods for monitoring marine fish cage farms in the Eastern Mediterranean and the main survey work is being undertaken in Greece. The research is carried out by 5 partners, Akvaplan-niva AS, Norway, Seas Ltd., Scotland, Institute of Marine Biology of Crete, Greece, Dunstaffnage Marine Laboratory, Scotland, and Institute of Marine Research of Kiel, Germany. Akvaplan- niva are coordinating the programme, from its offices in both Tromsø Norway and Athens. Further information about the project and partners can be found at the web site at www.meramed.com