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Introduction to the new EU Water Framework
Directive
The increasing demand by citizens and environmental organisations
for cleaner rivers and lakes, groundwater and coastal beaches
has been evident for considerable time. It has recently been
reconfirmed by a representative opinion poll Eurobarometer in all 25 EU countries:
When asked to list the five main environmental issues that
Europeans are worried about, averaged results for the EU25
show that nearly half of the respondents are worried about
“water pollution” (47%), with figures for individual
countries going up as far as 71%.
This demand by citizens is one of the main reasons why the
Commission has made water protection one of the priorities
of its work. The new European Water Policy will get polluted
waters clean again, and ensure clean waters are kept clean.
In achieving these objectives, the roles of citizens and citizens'
groups will be crucial. This is why a new European Water Policy
has to get citizens more involved.
European Water Policy has undergone a thorough restructuring
process, and a new Water Framework Directive adopted in 2000
will be the operational tool, setting the objectives for water
protection for the future.
The following will provide an overview on development, present
state and future of European Water Policy.
An early beginning
Early European water legislation began, in a "first
wave", with standards for those of our rivers and lakes
used for drinking water abstraction in 1975, and culminated
in 1980 in setting binding quality targets for our drinking
water. It also included quality objective legislation on fish
waters, shellfish waters, bathing waters and groundwaters.
Its main emission control element was the Dangerous Substances
Directive.
Addressing pollution from urban waste water and from agriculture
In 1988 the Frankfurt ministerial seminar on water reviewed
the existing legislation and identified a number of improvements
that could be made and gaps that could be filled. This resulted
in the second phase of water legislation, the first results
of this were, in 1991, the adoption of
- the Urban Waste Water Treatment Directive, providing
for secondary (biological) waste water treatment, and even
more stringent treatment where necessary.
- the Nitrates Directive, addressing water pollution by
nitrates from agriculture.
Other legislative results of these developments were Commission
proposals for action on
- a new Drinking Water Directive, reviewing the quality
standards and, where necessary, tightening them (adopted
November 1998),
- a Directive for Integrated Pollution and Prevention Control
(IPPC), adopted in 1996, addressing pollution from large
industrial installations.
Getting Europe 's waters cleaner, getting the citizen involved:
the new European water policy
Pressure for a fundamental rethink of Community water policy
came to a head in mid-1995: The Commission, which had already
been considering the need for a more global approach to water
policy, accepted requests from the European Parliament's environment
committee and from the Council of environment ministers.
Whilst EU actions of the past such as the Drinking Water
Directive and the Urban Waste Water Directive can duly be
considered milestones, European Water Policy has to address
the increasing awareness of citizens and other involved parties
for their water. At the same time water policy and water management
are to address problems in a coherent way. This is why the
new European Water Policy was developed in an open consultation
process involving all interested parties.
A Commission Communication was formally addressed to the
Council and the European Parliament, but at the same time
invited comment from all interested parties, such as local
and regional authorities, water users and non-governmental
organisations (NGOs). A score of organisations and individuals
responded in writing, most of the comments welcoming the broad
outline given by the Commission.
As the culmination of this open process a two day Water
Conference was hosted in May 1996. This Conference was attended
by some 250 delegates including representatives of Member
States, regional and local authorities, enforcement agencies,
water providers, industry, agriculture and, not least, consumers
and environmentalists.
The outcome of this consultation process was a widespread
consensus that, while considerable progress had been made
in tackling individual issues, the current water policy was
fragmented, in terms both of objectives and of means. All
parties agreed on the need for a single piece of framework
legislation to resolve these problems. In response to this,
the Commission presented a Proposal for a Water Framework
Directive with the following key aims:
- expanding the scope of water protection to all waters,
surface waters and groundwater
- achieving "good status" for all waters by a
set deadline
- water management based on river basins
- "combined approach" of emission limit values
and quality standards
- getting the prices right
- getting the citizen involved more closely
- streamlining legislation
The outline below shows how these elements are made operational
within the Directive.
A single system of water management: River basin management
The best model for a single system of water management is
management by river basin - the natural geographical and hydrological
unit - instead of according to administrative or political
boundaries. Initiatives taken forward by the States concerned
for the Maas , Schelde or Rhine river basins have served as
positive examples of this approach, with their cooperation
and joint objective-setting across Member State borders, or
in the case of the Rhine even beyond the EU territory. While
several Member States already take a river basin approach,
this is at present not the case everywhere. For each river
basin district - some of which will traverse national frontiers
- a "river basin management plan" will need to be
established and updated every six years, and this will provide
the context for the co-ordination requirements identified
above.
Co-ordination of objectives - good status for all waters
by a set deadline
There are a number of objectives in respect of which the
quality of water is protected. The key ones at European level
are general protection of the aquatic ecology, specific protection
of unique and valuable habitats, protection of drinking water
resources, and protection of bathing water. All these objectives
must be integrated for each river basin. It is clear that
the last three - special habitats, drinking water areas and
bathing water - apply only to specific bodies of water (those
supporting special wetlands; those identified for drinking
water abstraction; those generally used as bathing areas).
In contrast, ecological protection should apply to all waters:
the central requirement of the Treaty is that the environment
be protected to a high level in its entirety.
Surface water
Ecological protection
For this reason, a general requirement for ecological protection,
and a general minimum chemical standard, was introduced to
cover all surface waters. These are the two elements "good
ecological status" and "good chemical status".
Good ecological status is defined in Annex V of the Water
Framework Proposal, in terms of the quality of the biological
community, the hydrological characteristics and the chemical
characteristics. As no absolute standards for biological quality
can be set which apply across the Community, because of ecological
variability, the controls are specified as allowing only a
slight departure from the biological community which would
be expected in conditions of minimal anthropogenic impact.
A set of procedures for identifying that point for a given
body of water, and establishing particular chemical or hydromorphological
standards to achieve it, is provided, together with a system
for ensuring that each Member State interprets the procedure
in a consistent way (to ensure comparability). The system
is somewhat complicated, but this is inevitable given the
extent of ecological variability, and the large number of
parameters, which must be dealt with.
Chemical protection
Good chemical status is defined in terms of compliance with
all the quality standards established for chemical substances
at European level. The Directive also provides a mechanism
for renewing these standards and establishing new ones by
means of a prioritisation mechanism for hazardous chemicals.
This will ensure at least a minimum chemical quality, particularly
in relation to very toxic substances, everywhere in the Community.
Other uses
As mentioned above, the other uses or objectives for which
water is protected apply in specific areas, not everywhere.
Therefore, the obvious way to incorporate them is to designate
specific protection zones within the river basin which must
meet these different objectives. The overall plan of objectives
for the river basin will then require ecological and chemical
protection everywhere as a minimum, but where more stringent
requirements are needed for particular uses, zones will be
established and higher objectives set within them.
There is one other category of uses which does not fit into
this picture. It is the set of uses which adversely affect
the status of water but which are considered essential on
their own terms - they are overriding policy objectives. The
key examples are flood protection and essential drinking water
supply, and the problem is dealt with by providing derogations
from the requirement to achieve good status for these cases,
so long as all appropriate mitigation measures are taken.
Less clear-cut cases are navigation and power generation,
where the activity is open to alternative approaches (transport
can be switched to land, other means of power generation can
be used). Derogations are provided for those cases also, but
subject to three tests: that the alternatives are technically
impossible, that they are prohibitively expensive, or that
they produce a worse overall environmental result.
Groundwater
Chemical status
The case of groundwater is somewhat different. The presumption
in relation to groundwater should broadly be that it should
not be polluted at all. For this reason, setting chemical
quality standards may not be the best approach, as it gives
the impression of an allowed level of pollution to which Member
States can fill up. A very few such standards have been established
at European level for particular issues (nitrates, pesticides
and biocides), and these must always be adhered to. But for
general protection, we have taken another approach. It is
essentially a precautionary one. It comprises a prohibition
on direct discharges to groundwater, and (to cover indirect
discharges) a requirement to monitor groundwater bodies so
as to detect changes in chemical composition, and to reverse
any antropogenically induced upward pollution trend. Taken
together, these should ensure the protection of groundwater
from all contamination, according to the principle of minimum
anthropogenic impact.
Quantitative status
Quantity is also a major issue for groundwater. Briefly,
the issue can be put as follows. There is only a certain amount
of recharge into a groundwater each year, and of this recharge,
some is needed to support connected ecosystems (whether they
be surface water bodies, or terrestrial systems such as wetlands).
For good management, only that portion of the overall recharge
not needed by the ecology can be abstracted - this is the
sustainable resource, and the Directive limits abstraction
to that quantity.
One of the innovations of the Directive is that it provides
a framework for integrated management of groundwater and surface
water for the first time at European level.
Co-ordination of measures
There are a number of measures taken at Community level
to tackle particular pollution problems. Key examples are
the Urban Waste Water Treatment Directive and the Nitrates
Directive, which together tackle the problem of eutrophication
(as well as health effects such as microbial pollution in
bathing water areas and nitrates in drinking water); and the
Integrated Pollution Prevention and Control Directive, which
deals with chemical pollution. The aim is to co-ordinate the
application of these so as to meet the objectives established
above. This is done as follows.
First of all, the objectives are established for the river
basin as outlined in the previous section. Then an analysis
of human impact is conducted so as to determine how far from
the objective each body of water is. At this point, the effect
on the problems of each body of water of full implementation
of all existing legislation is considered. If the existing
legislation solves the problem, well and good, and the objective
of the framework Directive is attained. However, if it does
not, the Member State must identify exactly why, and design
whatever additional measures are needed to satisfy all the
objectives established. These might include stricter controls
on polluting emissions from industry and agriculture, or urban
waste water sources, say. This should ensure full co-ordination.
The combined approach
But there is a further aspect. Historically, there has been
a dichotomy in approach to pollution control at European level,
with some controls concentrating on what is achievable at
source, through the application of technology; and some dealing
with the needs of the receiving environment in the form of
quality objectives. Each approach has potential flaws. Source
controls alone can allow a cumulative pollution load which
is severely detrimental to the environment, where there is
a concentration of pollution sources. And quality standards
can underestimate the effect of a particular substance on
the ecosystem, due to the limitations in scientific knowledge
regarding dose-response relationships and the mechanics of
transport within the environment.
For this reason, a consensus has developed that both are
needed in practice - a combined approach. The Water Framework
Directive formalises this. It does so as follows. On the source
side, it requires that as part of the basic measures to be
taken in the river basin, all existing technology-driven source-based
controls must be implemented as a first step. But over and
above this, it also sets out a framework for developing further
such controls. The framework comprises the development of
a list of priority substances for action at EU level, prioritised
on the basis of risk; and then the design of the most cost-effective
set of measures to achieve load reduction of those substances,
taking into account both product and process sources.
On the effects side, it co-ordinates all the environmental
objectives in existing legislation, and provides a new overall
objective of good status for all waters, and requires that
where the measures taken on the source side are not sufficient
to achieve these objectives, additional ones are required.
The river basin management plan
All the elements of this analysis must be set out in a plan
for the river basin. The plan is a detailed account of how
the objectives set for the river basin (ecological status,
quantitative status, chemical status and protected area objectives)
are to be reached within the timescale required. The plan
will include all the results of the above analysis: the river
basin's characteristics, a review of the impact of human activity
on the status of waters in the basin, estimation of the effect
of existing legislation and the remaining "gap"
to meeting these objectives; and a set of measures designed
to fill the gap. One additional component is that an economic
analysis of water use within the river basin must be carried
out. This is to enable there to be a rational discussion on
the cost-effectiveness of the various possible measures. It
is essential that all interested parties are fully involved
in this discussion, and indeed in the preparation of the river
basin management plan as a whole. Which brings me to the final
major element of the proposal, the public participation requirements.
Public participation
In getting our waters clean, the role of citizens and
citizens' groups will be crucial.
There are two main reasons for an extension of public participation.
The first is that the decisions on the most appropriate measures
to achieve the objectives in the river basin management plan
will involve balancing the interests of various groups. The
economic analysis requirement is intended to provide a rational
basis for this, but it is essential that the process is open
to the scrutiny of those who will be affected.
The second reason concerns enforceability. The greater the
transparency in the establishment of objectives, the imposition
of measures, and the reporting of standards, the greater the
care Member States will take to implement the legislation
in good faith, and the greater the power of the citizens to
influence the direction of environmental protection, whether
through consultation or, if disagreement persists, through
the complaints procedures and the courts. Caring for Europe
's waters will require more involvement of citizens, interested
parties, non-governmental organisations (NGOs). To that end
the Water Framework Directive will require information and
consultation when river basin management plans are established:
the river basin management plan must be issued in draft, and
the background documentation on which the decisions are based
must be made accessible. Furthermore a biannual conference
in order to provide for a regular exchange of views and experiences
in implementation will be organised. Too often in the past
implementation has been left unexamined until it is too late
- until Member States are already woefully behind schedule
and out of compliance. The Framework Directive, by establishing
very early on a network for the exchange of information and
experience between water professionals throughout the Community
will ensure this does not happen.
Streamlining legislation: seven old directives to be repealed
One advantage of the framework directive approach, in its
own way a significant one, is that it will rationalise the
Community's water legislation by replacing seven of the "first
wave" directives: those on surface water and is two related
directives on measurement methods and sampling frequencies
and exchanges of information on fresh water quality; the fish
water, shellfish water, and groundwater directives; and the
directive on dangerous substances discharges. The operative
provisions of these directives will be taken over in the framework
directive, allowing them to be repealed.
Getting the prices right
The need to conserve adequate supplies of a resource for
which demand is continuously increasing is also one of the
drivers behind what is arguably one of the Directives's most
important innovations - the introduction of pricing. Adequate
water pricing acts as an incentive for the sustainable use
of water resources and thus helps to achieve the environmental
objectives under the Directive.
Member States will be required to ensure that the price
charged to water consumers - such as for the abstraction and
distribution of fresh water and the collection and treatment
of waste water - reflects the true costs. Whereas this principle
has a long tradition in some countries, this is currently
not the case in others. However, derogations will be possible,
e.g. in less-favoured areas or to provide basic services at
an affordable price.
Conclusion
Much progress has been made in water protection in Europe
, in individual Member States, but also in tackling significant
problems at European level. But Europe 's waters are still
in need of increased efforts to get them clean or to keep
them clean. After 30 years of European water legislation,
this demand is expressed, not only by the scientific community
and other experts, but to an ever increasing extent by citizens
and environmental organisations. We should take up the challenge
of water protection, one of the great challenges for the European
Union in the new millennium. Let us seize the initiative generated
by the political process on the Water Framework Directive
for the benefit of all Europe 's citizens and waters:
- Getting Europe 's waters cleaner
- Getting the citizens involved.
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