The Precautionary Principle and approach
Introduction
The Precautionary Principle is one of the key elements for
policy decisions concerning environmental protection and
management. It is applied in the circumstances where there are
reasonable grounds for concern that an activity is, or could, cause
harm but where there is uncertainty about the probability of the
risk and the degree of harm.
The Precautionary Principle has been endorsed internationally
on many occasions. At the Earth Summit meeting at Rio in 1992,
World leaders agreed Agenda 21, which advocated the widespread
application of the Precautionary Principle in the following
terms:
'In order to protect the environment, the precautionary
approach shall be widely applied by States according to their
capabilities. Where there are threats of serious or irreversible
damage, lack of full scientific certainty shall not be used as a
reason for postponing cost-effective measures to prevent
environmental degradation.' (Principle 15)
In Fisheries Management this precautionary approach has been
defined in two international instruments:
- the FAO Code of Conduct for Responsible Fisheries (CCRF);
and
- the Agreement for the Implementation of the Provisions of the
United Nations Convention on the Law of the Sea of 10 December 1982
relating to the Conservation and Management of Straddling Fish
Stocks and Highly Migratory Fish Stocks (UNIA).
Both of these share common wording and ideas. The wording used
in the CCRF is:
'States should apply the precautionary approach widely to
conservation, management and exploitation of living aquatic
resources in order to protect them and preserve the aquatic
environment. The absence of adequate scientific information should
not be used as a reason for postponin or failing to take
conservation and management measures.'
The CCRF is a voluntary, non-binding agreement, while the UNIA
is now a binding agreement amongst signatory States and entered
into force on 11 December 2001.
Precautionary Principle and the European Union
The EU Treaty contains a reference to the Precautionary
Principle, but does not define it. The Council sought clarification
by requesting the Commission to develop clear and effective
guidelines for the application of the principle.
In 2000, the European Commission adopted a Communication on
the use of the Precautionary Principle, which set out a number of
steps to be followed. These were:
if a preliminary scientific evaluation shows that there are
reasonable grounds for concern that a particular activity might
lead to damaging effects on the environment, or on human, animal or
plant health, which would be inconsistent with the protection
normally afforded to these within the European Community, the
Precautionary Principle is triggered;
decision-makers then have to determine what action to take.
They should take account of the potential consequences of taking no
action, the uncertainties inherent in the scientific evaluation,
and they should consult interested parties on the possible ways of
managing the risk. Measures should be proportionate to the level of
risk, and to the desired level of protection. They should be
provisional in nature pending the availability of more reliable
scientific data;
action is then undertaken to obtain further information
enabling a more objective assessment of the risk. The measures
taken to manage the risk should be maintained so long as the
scientific information remains inconclusive and the risk
unacceptable.
European implementation
Following a request from the European Commission, the
International Council for the Exploration of the Sea (ICES) have
developed a procedure for implementing a precautionary approach in
its advice to the Commission on fish stocks and future catch
levels. This is done by setting reference points - in effect
trigger levels at which management action should be taken. ICES
identify two types of reference points: 'limit' and
'precautionary'. The intention is that fish stocks are managed so
they do not exceed the precautionary limit reference point.
Fisheries managers can, therefore, be reasonably confident that
limit reference points - at which there is a serious risk of stock
collapse - are never reached.
The precautionary reference figures produced by ICES are used
by Member States to negotiate catch quotas. Unfortunately, these
negotiations often result in quotas exceeding the ICES
recommendations. Many fish stocks are now at levels below the
precautionary reference point and some are below the limit
reference point, thereby requiring drastic recovery plans.
Limitations of the precautionary approach as currently
applied
Over the last few decades, action under the Common Fisheries
Policy (CFP) has been far from being effectively precautionary. In
January 2003, a new CFP was issued. Since then things have begun to
improve:
- Catch quotas tend to be set too high, and neither allowable
catch nor recorded landings reflect actual mortality. Catch quotas
are set a target for 'catch' which only relates to what is
officially landed. Other unquantified elements of mortality arise
through (i) bycatches, (ii) discards, and (iii) misreported
landings. The incentives for fishermen 'at the point of catch' are
inconsistent with the overall objective of sustainable use for the
fishery as a whole. In the mixed demersal fishery of most European
waters, this creates huge wastage of fish through the anomalous
incentive for fishers to catch and discard species which have
reached their catch quota for the year, and only land the most
marketable individuals of species which are below the catch quota.
Although the problem of differences in ICES quota advice and that
set by the member States has not been addressed, the European
Commission has recently introduced proposals to reduce discarding
and also to encourage the use of more 'environmentally-friendly'
fishing gear
- The precautionary approach has only been applied to a selected
sub-set of commercial fish stocks for which ICES advice has been
requested. Stocks of other species have not yet received such
consideration, for example, sharks, skaltes and rays (collectively
known as elasmobranchs) and many deep-water
species whose stocks are particularly sensitive to
fishing;
- The precautionary approach, as has been applied, does not
address the wider effects of fisheries on the ecosystem and marine
environment. However, recently measures have been introduced to
improve this. For example, emergency protection for the Darwin
Mounds, an area for the deep water coral Lophelia pertusa, was
introduced under the CFP and is permanently protected from August
2004, whilst in February 2004, other deep water coral sites in the
Azores, Madeira and the Canary Islands were also proposed for
protection and in March 2004 regulations were introduced to reduce
harbour
porpoise bycatch, which involve the use of 'pingers' on
bottom-set gillnets and entangling nets.
These latter issues may be addressed through an
ecosystem-based approach to fisheries management
and wildlife conservation. This aims to protect or restore the
function, structure, and species composition of an ecosystem while
providing for its sustainable socio-economic use. However, quite
clearly, the current implementation of the Precautionary Principle
in relation to fisheries management is partial and
inadequate.
Effective precautionary approaches point towards:
for all fisheries, assessing the need for closer oversight of
actual fish mortality, rather than landings. This may involve more
effective monitoring of fishing effort at sea - e.g. via broadening
the use of vessel monitoring systems;
assessing the need to decrease outputs (i.e. lower catch
limits) especially for fisheries at the limit;
widening the approach taken through input controls - e.g.
through spatial management using permanent and temporary exclusion
zones, or by limiting days at sea;
considering the need to develop indicators (both for the
fishery and for the wider environment) to provide feedback on the
effects of fishing activity;
reviewing the responsiveness of existing management structures
to different interests;
non-quota and new fisheries should be the subject of
environmental assessment and improved methods of control;
habitats and species afforded strict protection under EC
legislation should be subject to a high level of precaution.
Strategic implications
In the longer term, we see the need to build confidence
amongst all interest groups that a sustainable fishery is a
desirable outcome. This will include removing the fear of
'precaution' as a management principle, encouraging confidence that
precaution will not be used unreasonably to restrict sustainable
fishing activity, and thereby create a permissive environment for
decision-makers to take precautionary decisions.
We see the need to move towards management regimes which
reward, and foster the values of, good stewardship. The
effectiveness of precaution will be greatly enhanced where it
reinforces this kind of ownership and stewardship of the resource.
Under these circumstances precautionary measures are more likely to
be widely supported and implemented by fishermen, meanwhile
reducing reliance on stringent (and costly) enforcement
mechanisms.
Further reading
Commission of the European Communities. Communication from
the Commission on the use of the Precautionary
Principle.2000(1).
Doulman, D.J. 1995. Structure and process of the 1993-1995
United Nations conference on straddling fish stocks and highly
migratory fish stocks. FAO Fisheries Circular No.
898.81p.
FAO 1999.
The state of world fisheries and aquaculture.
Food and Agriculture Organisation of the United Nations. Rome.
112p.
http://www.fao.org./
FAO 1995a .Code of conduct for responsible fisheries.Food
and Agriculture Organisation of the United Nations. Rome.
41p.
FAO 1995b. Precautionary approach to capture fisheries and
species introductions.FAO Fisheries Tech. Pap. 350 part 1,
Food and Agriculture Organisation of the United Nations. Rome.
54p.
ICES 1997.
Report of the Precautionary Approach to
Fisheries Management. Copenhagen, 5-11 February 1997. ICES CM
1997/Assess: 7.
http://www.ices.dk./
ICES 1998. Report of the Precautionary approach to
Fisheries Management. Copenhagen, 3-6 February 1998. ICES CM
1998/ACFM: 10.
Jordan, A. and T. O'Riordan. 1999. The Precautionary
Principle in contemporary environmental policy and politics.
Pages 15-35 in C. Raffensperger and J.A. Tickner, eds. Protecting
public health and the environment: implementing the Precautionary
Principle. Island Press, Washington, EC.
Myers, R.A., J.A. Hutchings, and N.J. Barrowman. 1997. Why
do fish stocks collapse? The example of cod in Atlantic
Canada. Ecological Applications 7(1): 91-106.
Rio Declaration 1992. Rio Declaration on environment and
development. ISBN 9-21-100509.
Rosenberg, A.A., M.J. Fogarty, M.P. Sissenwine, J.R.
Beddington and J.G. Shepherd 1993. Achieving sustainable use of
renewable resources. Science 262: 828-829.
Rosenberg, A.A. 2002. The precautionary approach from a
manager's perspective. Bulletin of Marine Science 70:
577-588.
World Humanity Action Trust. 2000. Governance for a
sustainable future: II Fishing for the future. World Humanity
Action Trust, London. 67p.