Summary
of groundwater aspects of the Water Framework Directive
Introduction
Environmental objectives for groundwater
Groundwater Status
Process and timetable
Explanation of aspects of the process
Repeal of existing legislation
Definitions of relevant terms used in the Directive
Introduction
The EU Water
Framework Directive came into force on 22 December 2000.
It was introduced in response to a consensus across Europe
that water policy was fragmented. This single piece of framework
legislation expands the scope of water protection to all bodies
of water, surface water and groundwater, with the aim of achieving
‘good status’ by 2015.
Assessment and management of water bodies will be carried
out on a River Basin District basis. Water bodies include
lakes, reaches of rivers and groundwater bodies. Groundwater
bodies are defined as distinct volumes of groundwater
within an aquifer or aquifers. The definition of aquifer
used in the Directive means that most of the rocks in the
UK that were previously classified as non-aquifer material
are now considered to be aquifers. Little of the UK is not
underlain by a groundwater body.
Environmental objectives for groundwater
The Directive sets out a series of environmental objectives
to be met. Those specifically for groundwater are:
- to implement measures to prevent or limit the input
of pollutants into groundwater and to prevent deterioration
of groundwater;
- to protect, enhance and restore all bodies of groundwater,
ensure a balance between abstraction and recharge of groundwater,
with the aim of achieving ‘good groundwater status’
within 15 years of the Directive coming into force, except
under certain special circumstances;
- to implement measures to reverse any significant and
sustained upward trend in the concentration of any pollutant
resulting from the impact of human activity in order to progressively
reduce the pollution of groundwater; and
- to ensure compliance with the relevant standards and
objectives for ‘Protected Areas’ within 15 years
of Directive implementation (includes groundwater bodies from
which abstraction for human consumption exceeds 10 m3/d or
serves greater than 50 persons).
Less stringent objectives for specific bodies of water may
be set where these are so affected by human activity or their
natural condition is such that it would be unfeasible or disproportionately
expensive to reach good status. The 15-year target date can
be extended where there are reasonable grounds.
Groundwater Status
Groundwater status consists of quantitative and chemical components.
Groundwater levels will be used as a measure of quantitative
status. The levels in the groundwater body should be such
that the available groundwater resource (i.e. the long-term
average rate of overall groundwater recharge to the body less
the long term annual rate of flow required to achieve the
ecological quality objectives for associated surface waters)
is not exceeded by the long-term annual average rate of abstraction.
Chemical status is measured by concentrations of pollutants
and changes in electrical conductivity in the groundwater
body such that it:
- does not exhibit effects of saline or other intrusions;
- does not exceed the Community quality standards;
- would not result in failure to achieve the environmental
objectives in associated surface waters or terrestrial ecosystems.
Process and timetable
The process and timetable for Member States to achieve the
environmental objectives, and significant deadlines for the
Community to undertake actions within the Directive, are as
follows (timings are relative to the date when the Directice
came into force – 22 December 2000):
Within 2 years
- Commission to propose specific measures to establish
criteria for assessing good groundwater chemical status and
identifying trends in pollutants
Within 4 years
- identification of River Basin Districts and assignment
of groundwater bodies to these Districts
- characterisation of the Districts
- identification and listing of protected areas
- review of the impact of human activity on the status
of surface water and groundwater
- classification of water bodies, including those that
are at risk of failing to meet environmental objectives.
The latter must generally be characterised in more detail.
- economic analysis of water use
Within 5 years
- if not already set by Commission, Member States to
establish criteria for assessing good groundwater chemical
status and identifying trends in pollutants
Within 6 years
- groundwater monitoring programme established
- Commission to put in place emission controls for point
sources and environmental quality standards for substances
on first list of priority substances
Within 9 years
- establishment of River Basin Management Plans including
a Programme of Measures designed to enable objectives to be
met.
Within 10 years
- appropriate water pricing policies put in place
Within 15 years
- ensure ‘good status’ is achieved for all
water bodies except for exceptional cases.
Explanation of aspects of the process
Click on the links below:
Characterisation of groundwater
bodies
Review of the impact of human activity
on groundwaters
Monitoring of groundwater bodies
Waters used for abstraction of
drinking water
Programmes of Measures
The Directive also addresses the requirement for:
- an economic analysis of water use;
- recovery of costs for water services;
- provision of public information and consultation.
Explanations of these aspects can be found at sites listed
on the links page.
Repeal of existing legislation
Certain existing legislation will be repealed in due course
as a result of the Water Framework Directive. The Groundwater
Directive (80/68/EEC), protecting groundwater from pollution
by certain dangerous substances, will be repealed in 2013.
The Nitrates
Directive (91/676/EEC) will remain in force.
Definitions of relevant terms used
in the Directive
Groundwater - all
water which is below the surface of the ground in the saturated
zone and in direct contact with the ground or subsoil.
Aquifer - a subsurface
layer or layers of rock or other geological strata of sufficient
porosity and permeability to allow either a significant flow
of groundwater or the abstraction of significant quantities
of groundwater.
Body of groundwater -
a distinct volume of groundwater within an aquifer or aquifers.
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