| VIII. FISHERIES AND AQUACULTURE
8.1. Status and Trends
Coastal waters serve as important nursery, feeding and spawning
areas for the world's fisheries, and much of the global marine fish
catch comes from important habitats in nearshore waters, inter-tidal
areas, estuaries and bays. Europe supports an intensive fishing
industry. In the North Sea, for example, each year 50-60% of the
total biomass of the main commercial fish stocks is removed (Seas
at Risk 1994).
The contribution of fishing to the GDP of European countries (usually
less than 1% ) (European Commission
1994a) belies the importance of its role in the economies of
coastal communities, both directly and indirectly. It is estimated
that for every job at sea, there are four or five on shore in fishing-related
industries (European Commission 1994a).
Serious depletion of fish stocks (from overfishing and discarding
bycatch, improved fishing methods, climatic change and pollution)
has led to the forced reduction in catches and decreased employment
opportunities.(European Commission
1994 , (Iribarne and Jacques), (VASAB 1994) Fishing fleets
now tend to concentrate in fewer and larger ports, and the smaller
ports are suffering, particularly where there are few alternatives
to the fishing and fish processing industries.(European
Commission 1995), (European Commission
1994) The Atlantic Arc region, which has few large ports, is
especially likely to suffer in the face of these trends. Indeed,
the significant reduction in fleets as a result of EU regulations
is already having an impact here (Shipman 1996). In general,
the decline in offshore fisheries has led to increased pressure
on coastal fisheries (OECD 1993).
In the Mediterranean, for example, high seas trawlers have been
forced to move closer to shore, competing with inshore artisanal
trawling and other activities (UNEP
1996). Unless stricter policy measures are implemented,
the decline in fishing is likely to continue.
There is an increasing trend towards fish farming, however, with
particular interest in shellfish (Iribarne and Jacques). In
the European Union, for example, farmed fish and shellfish account
for around 7% of aquaculture output worldwide, providing employment
for more than 80,000 people in coastal areas (European
Commission 1994a). The continued growth of the industry
will depend in part on its ability to overcome environmental problems
and avoid increased production costs (European
Commission 1995). If successful, the industry can provide
new sources of employment, and reduce Europe's dependence on imported
fish.
8.2. Impacts
Environmental impacts of fishing include overfishing of commercial
fish stocks, damage to the marine ecosystem as a result of loss
or discarded fishing gear, the incidental take of non-target species
(including marine mammals), oil pollution and litter from fishing
vessels, and pollution from fish processing plants. These impacts,
combined with problems of coastal and marine habitat destruction,
land and marine-based pollution, and the introduction of alien species,
have serious consequences for aquatic diversity, and ultimately
for the health of fish stocks themselves (Intermediate
Technology 1996).
Impacts from aquaculture are also a serious concern, particularly
if a larger industry develops. The discharge of wastes (which may
include alien species, anti-fouling pesticides, antibiotics and
other pharmaceuticals, organic matter and nutrients) to the surrounding
sea can affect local fish populations, contribute to eutrophication
and upset the ecological balance, particularly in semi-enclosed
coastal areas.(UNEP 1995), (FAO
1994), (HELCOM 1993),
(UNEP 1996) In oligotrophic environments such as the Mediterranean,
aquaculture may displace fishing grounds, attract dolphins and compete
with traditional fisheries. Moreover, there are concerns that biotechnology
and/or breeding techniques could have negative impacts on wild species
in the event that genetically altered species escape and interbreed
(UNEP 1996). In some cases,
(e.g. salmon farming) aquaculture may be a resource intensive enterprise.
According to one expert, "Salmon farming in cages requires lots
of resources collected by fishing vessels operating over vast marine
ecosystems. The marine water surface area required to produce the
food given to the salmon in the cages is about 1 km² per ton
of salmon. This area is similar independently of whether a salmon
is caged farmed or caught out in the sea. The ecological footprint
of the salmon farm is as much as about 50 000 times larger than
the areas of the cages." (Folke 1995)
8.3. Opportunities
| “The conservation of aquatic biodiversity in situ
has always been central to the strategies of nurture fisheries.
These strategies adopted by artisanal fishing communities
over millennia differ markedly from the modern industrial
approach to fishing, using capture fishery strategies.
Nurture fishery technologies are necessarily selective,
passive, low-energy and ecologically efficient. They may not
bring in the biggest catch in the short term, but they ensure
the sustainability of the fishery through their harmonious
interaction with the dynamics of the ecosystem, on which depends
the aquatic biodiversity?” - Intermediate Technology |
As a follow-up to the first Earth Summit in 1992 and the subsequent
UN Conference on Straddling Fish Stocks and Highly Migratory Fish
Stocks, FAO undertook the development of a global Code of Conduct
for Responsible Fisheries. An extensive process of consultation
was conducted, and was unanimously approved in October, 1995 by
the FAO Conference. The Code is directed toward "members and non-members
of FAO, fishing entities, subregional, regional and global organizations,
whether governmental or non-governmental, and all persons concerned
with the conservation of fishery resources and management and development
of fisheries, such as fishers, those engaged in processing and marketing
of fish and fishery products and other users of the aquatic environment
in relation to fisheries. "(FAO 1995)
The Code is broad in scope, covering fisheries management and operations,
aquaculture, integration of fisheries into coastal area management,
post-harvest practices and trade, and fisheries research. Its measures
relate not only to technical issues, but also to social issues such
as the fair and equitable treatment of fishworkers. If it is widely
implemented, the Code will represent a major step forward in the
conservation of marine biodiversity.
| “Multi-species aquaculture or ‘polyculture’ is based on
the harmonious stocking of different varieties of fish species
at different levels of population, using an understanding
of the production cycle and energy flow through the pond.
There are planktonic feeders (at the pond surface and in mid-water)
which feed directly off the ‘phytoplankton’ and ‘zooplankton’
produced by the natural productivity of the pond. The faeces
they produce further enhance the productivity of the pond,
as does pond manuring (with agricultural and household residues).
Fish species which feed on larger organisms in mid-water (small
fish, insects, etc.) and the pond bottom (snails, worms, etc.)
are also stocked. The result is that energy flow and transformation
are extremely efficient. If this method of conservation in
situ is to be sustained by traditional aquaculture, then
attention needs to be focused on decentralized production,
using diverse, environmentally sensitive techniques. Protection
from introduced species and diseases is also required.” –
Intermediate Technology |
8.4. Guidelines for Fisheries and Aquaculture
The 1995 FAO Code of Conduct for Responsible Fisheries, particularly
Article 10 on the Integration of Fisheries into Coastal Area Management,
should be implemented by all coastal states and fishing communities.
The UN Agreement for Conservation and Management of Straddling Fish
Stocks and Highly Migratory Fish Stocks (New York, 1995) should
also be implemented as quickly as possible.
Fisheries management should adopt a precautionary approach in which
the fundamental health of coastal and marine ecosystems is maintained.
A lack of adequate data should not be considered grounds for postponing
effective conservation measures. The optimum sustainable yield should
be considered as a replacement for the maximum sustainable yield
of any given fishery.
Wherever possible, capture fishery strategies should be replaced
by nurture fishery strategies managed by fishing communities. Capture
methods which seriously damage or degrade coastal and marine ecosystems
should be phased out, with priority given to environmentally safe
fishing methods.
The development and use of increasingly selective fishing gear
and methods should be encouraged for both target and non-target
species. By-catch, discards and waste should be minimised to the
maximum extent possible. Large-scale pelagic driftnet fishing should
be ceased in accordance with the United Nations Resolution on this
subject.
For stocks which are currently over-exploited, particularly where
spawning stocks are depleted or where the ecosystem has been seriously
damaged, fishing efforts should be reduced or ceased until stocks
have recovered.
Aquaculture
| Greenpeace Principles for Ecologically Responsible, Low
Impact Fisheries To minimize the risk of irreversible
damage, the intensity of fishing should not substantially
or permanently distort the character of the ecosystem. To
achieve this, target stocks should be maintained at a high
proportion of the biomass that would occur in the absence
of fishing.
As a rule, a fishery must not jeopardize the ability of
any species to withstand natural or human induced fluctuations
in the environment.
A fishery must not endanger any species or population,
nor inhibit the recovery of any that are depleted, threatened
or endangered.
The catch of non-target species or undersized fish (bycatch)
in fishing operations must be reduced to levels approaching
zero. Any remaining bycatch should not be discarded, but
instead brought to shore, unless it can be returned to the
sea alive and in a healthy condition.
The destructive impacts of a fishing activity on habitats
must be eliminated (e.g. damage to coral reefs, seagrass
beds, bottom substrate).
Wasteful forms of fish production and fishing for wasteful
purposes, such as those which involve only a lethal harvest
of roe, must be eliminated.
Industrial reduction fisheries must be treated with particular
caution because of the potential for serious food web impacts
caused by removal of such large amounts of the marine biomass
at critical trophic levels.
Toxic, persistent, or bioaccumulative substances must not
be part of the production process. Compounds which are not
hazardous should be either recycled, reused or reprocessed.
Total energy consumption of the product cycle, including
fisheries operations transport, processing and distribution,
must be minimized.
CFCs, HCFCs, HFCs and other ozone depleting substances
and refrigerants, as well as substances that contribute
to global warming must be eliminated from the production
cycle wherever alternatives exist.
Packaging must be minimized in the first instance and should
be reusable or recyclable.
|
Aquaculture can be developed in ways which do not degrade coastal
and marine biodiversity. Integrated systems will be more sustainable
than monocultures, for example by the combined culturing of seaweeds,
mussels and salmon.
Due to their extensive space and water requirements, hatcheries
will have fewer impacts on the surrounding environment if they are
located within developed areas of the coast and where road access
already exists. If possible, they should be contained within existing
buildings.
Contamination problems can be significantly reduced by locating
large-scale production units in exposed or semi-exposed locations
in the sea, in water depths of at least 40 metres. However, special
attention must then be paid to the increased risks of farmed fish
escaping to the wild. In any event, such units should be located
away from sea grass communities or other sensitive habitats, as
well as recreational and fishing areas. Support facilities should
be located onshore in previously developed sites. Fish packing and/or
processing units should be located onshore, perhaps in existing
industrial sites.
Small-scale production units should be located onshore, set back
from the beach, in areas with good road access. Fish tanks should
be set in the ground, with pipelines and services buried underground.
Birds or wild fish should be deterred from intrusion through the
use of nets.
All steps should be taken to prevent escapes of farmed species
and interactions with wild species. Site-specific contingency plans
will help minimise the impacts of an escape of a significant number
of fish.
Biosafety measures can be applied to minimise the effects and transfers
and introductions of alien species, including prior impact analysis,
quarantine, and when and where necessary, eradication measures or
operations closure. The International Council for the Exploration
of the Sea (ICES) Code of Practice on the Introductions and Transfers
of Marine Organisms (1994) provides important guidelines on this
subject.
The control and prevention of diseases and parasites should be
carefully considered. Techniques include vaccination, dietary measures,
frequent and detailed health inspections, optimal stocking densities,
careful handling and avoidance of unnecessary disturbance of fish,
disinfection of transportation equipment and the use of foot baths
at production facilities. In addition, fallowing of sites should
be considered where possible to minimise outbreaks of disease and/or
parasites and to allow the recovery of benthic areas. Any diseased
stock should be treated or removed, and under no circumstances be
allowed to enter the marine environment.
Dead or dying fish should be removed as quickly as possible and
safely disposed of.
Fish farms can minimise nutrient discharges and losses by developing
and utilising appropriate feeding methods and fish feed (predominantly
dry).
Special treatment plants can be an effective way to eliminate solid
wastes, chemical and pharmaceutical additives, and nutrients from
effluents or other discharges to the sea. Discharge pipe outlets
should not be located near intake pipes of other installations.
In some cases, treated effluent water from fish farms can be used
for agricultural irrigation.
The use of toxic chemicals at fish farms should be banned. Net
cages can be washed or dried in place of the use of toxic anti-fouling
compounds.
REFERENCES: Fisheries and Aquaculture
- European Commission, Directorate General for Fisheries, "The
New Common Fisheries Policy", ISBN 92-826-7570-X, 1994.
- Folke, C., "Marine Biodiversity and Ecosystem Services as the
foundation for Social and Economic Development in Coastal Areas,
in Hedlund, L., Hägerhäll, B., Johannesson, K., "Biodiversity
and Sustainable Use of Coastal Waters: 21-25 August 1995, Tjärnö
Marine Biological Laboratory, Sweden", Discussion paper no 2,
Swedish Scientific Committee on Biological Diversity, November,
1995.
- Food and Agriculture Organization of the United Nations (FAO),
"Code of Conduct for Responsible Fisheries", Rome 1995.
- Food and Agriculture Organization of the United Nations (FAO),
"Technical Consultation on the Code of Conduct for Responsible
Fishing, Guidelines for the Integration of Fisheries into Coastal
Area Management", Rome, 26 September - 5 October 1994.
- Greenpeace International, "Greenpeace Principles for Ecologically
Responsible Fisheries", Preliminary Document, Amsterdam, February,
1996.
- HELCOM, Recommendation 18/3 "Measures Aimed at the Reduction
of Discharges from Marine Fish Farming", 12 March 1997.
- ICES, "Code of Practice on the Introductions and Transfers
of Marine Organisms 1994", International Council for the Exploration
of the Sea, September 1995.
- Intermediate Technology, "Fisherfolk safeguarding Aquatic Diversity
through their Fishing Techniques", Intermediate Technology Development
Group, UK, 1996.
- NASCO, "Resolution by the Parties to the Convention for the
Conservation of Salmon in the North Atlantic Ocean to Minimise
Impacts from Salmon Aquaculture on the Wild Salmon Stocks", CNL
(94) 53, 1994.
- Planning Authority (Malta), "Policy & Design Guidance,
Fishfarming", May, 1994.
- SEAS AT RISK, "Final Declaration of the First European Seas
at Risk Conference" Copenhagen, 1994.
- Swedish Society for Nature Conservation, "Marine Environment
Action Plan," May, 1990.
- WWF International and Greenpeace International, "General Principles
for a Mediterranean Fisheries Management Regime", June 1997.
|