Title: Ecological Status Classification of Surface Waters
1Ecological Status Classification of Surface
Waters SWAP Meeting A Challenge for
Implementation of the Water Framework
Directive Murray, N. Eisenreich, S. Heiskanen,
AS van de Bund, W Cardoso, AC
2Outline
- Ecological status in the Water Framework
Directive - State of the art in monitoring classification
of ecological status in MS - Setting the management goals Problems of WFD
Intercalibration
3Ecological Status in WFD
- Needs to be determined using BIOLOGICAL quality
elements - Biological status is the basis for classification
- Ecological classification sets the managements
goals for RBMP - border between good and moderate is determined
through intercalibration
4Surface Water Status
- Determined by poorer of chemical and ecological
status - Chemical status concentrations of specific
pollutants not exceeding specified levels - Ecological status expression of the quality of
the structure and functioning of aquatic
ecosystems
5Quality Elements for Ecological Status
Biological Quality Elements
6 Biological quality elements
Rivers Lakes Estuaries Coastal
waters Phytoplankton X
X X Macrophytes X X
X X Zoobenthos X X
X X Fish X
X X
7Assessment of Ecological Status
Reference value
Biological quality elements
8To assess ecological status you need
- Typology (A or B)
- Type-specific reference conditions (for all QE)
- Monitoring programmes (including all QE)
- which parameters to monitor?
- agreement about class boundaries
9Interpretation of Normative Definitions
- What are slight, moderate, major and
severe deviations? - Need for equal level of ambition in WFD
implementation intercalibration
10Quantifying ecological status problem of errors
11Quality elements in national classification
systems for rivers (REFCOND data from 15
countries)
12Compatibility of river methods with WFD (REFCOND
data from 15 countries)
13Normative definitions of ecological status
classification
(nearly) totally undisturbed slight
alterations moderate alterations major
alterations severe alterations
14Selection of intercalibration sites
15Intercalibration should include
- Rivers, lakes, coastal waters from all ecoregions
- different quality elements for rivers
- macroinvertebrates
- fish
- aquatic flora (macrophytes, diatoms)
16Requirements for intercalibration
- Selection of intercalibration sites
- agreement on class boundaries
- Data
- Intercalibration exercise
- Data from different quality elements
- comparable sampling methods
- knowledge of sources of error
17Surface water status in WFD
- Needs to be determined by poorer of chemical and
ecological status - Chemical status concentrations of specific
pollutants not exceeding specified levels - Ecological status Ecological Quality Ratio based
on biological indicator values related to
reference conditions
18Ecological Status in WFD
- Needs to be assessed using BIOLOGICAL quality
elements - Ecological classification sets the managements
goals for River Basin Plans - Intercalibration sets the quality criteria for
restoration targets of water bodies
19Ecological Status Assessment
- Following steps Information required
- Characterization of surface water types
- Type-specific reference conditions (for all QE)
- Biological monitoring data available (all QE)
- Classification of EQR (for all QE)
- Agreement of the normative definitions slight,
moderate, major and severe deviations from
minimally disturbed conditions - intercalibration
20Characterization of surface water types
- Need to have sufficiently large types to enable
reporting intercalibration - Large types may not be ecologically relevant ?
Difficult to establish reference conditions - Requires a network of reference sites, where
biological data available for testing typology
based on morphological physical factors
21Challenge of Reference conditions
- Several potential methods available
- Spatial reference sites, historical data,
predictive modelling, stressor-response
trajectories (curve fitting ), paleoecology,
expert judgement, etc. - Problems with biological data availability,
quality comparability, and high initial costs
of some methods - Comparisons of different methods required (may
not always lead to same results) - Need to agree on definitions of totally, or
nearly, undisturbed conditions (what is
considered pristine?)
22Setting the Reference Values ofbiological
quality elements
1. Spatially derived Reference conditions
similar water body types
23Setting the Reference Values ofbiological
quality elements (2)
2. Pressure-response relationships
Observed or modeled range of change
Biological indicator value
Modeled Reference conditions
Environmental pressure value
24Setting the Reference Values ofBiological
Quality Elements (3)
3. Hindcasting based on statistical models
Observed range of change
Biological indicator value
Hindcasted Reference conditions
Time before significant human impact (?)
Time (decades, centuries?)
25Challenge of Classification
- Agreement of WFD normative definitions slight,
moderate, major and severe deviations from
totally, or nearly, undisturbed conditions - Statistical errors related to variability in
reference conditions and in biological data need
to be estimated and considered - Indicators have different responses to different
pressures ? indicator-stress relationships need
to be established
26Problem of Errors in Setting the Class Boundaries
- Natural variability of reference values will
influence the setting of the borders for EQR
scale - Selection of a narrow range (e.g. 95 CI of the
data) may result in higher probability to
misclassify sites in lower class - Selecting a wider range (e.g. 10th percentile)
may result in higher probability to classify
sites too high (I.e. impact is not detected)
Johnson, R., 2001
27Different Indices - Different EQR scales
28Challenge of Intercalibration
- WFD requires intercalibration of the Member
States Ecological Quality assessment systems in
2006. - Objective is to compare and harmonize EQR class
boundaries between Member States within the same
ecoregion - Selection of Intercalibration sites should be
carried out in 2003 - Harmonised typology required
- Scarcity of biological data may hamper progress
of intercalibration process, especially selection
of sites
29Inter-calibration of the EQR Scale
Environmental pressure
30Setting the yard stick
Biotic quality indicator
31Looking ahead Research needs for FP6 Ecological
Water Quality Indicators
- Develop new indicators and indicator metrics for
cost efficient monitoring and reliable assessment
- Develop practical reliable methods to establish
reference conditions - Develop integrated biological indices to assess
functional health of aquatic ecosystems - Develop indicators to allow detection of
ecosystem alteration due to large scale
(climatic) vs. local anthropogenic changes
32Looking ahead Needs for FP6
- Need for a long term initiative for development
and harmonization of the ecological quality
classification - Good data is needed on biological quality
elements and their responses on pressures - European scale initiative on harmonized
biological data collection on surface waters
would yield - Added value for development and comparability of
assessment methods required by WFD - possibility to test scientific hypothesis on
ecological responses and changes across large
spatial (Europe) and temporal scales (e.g.
climate change)
33European Centre for Ecological Water Quality and
Intercalibration
- FP6 Launching a Long-term/ permanent, scientific
and technical focal point for comparison,
intercalibration, and harmonisation of ecological
assessment systems - Initiative taken during WFD Common Implementation
Strategy Work in 2001 - Preparations carried out by JRC-IES/ IMW-unit
34Justification
- First intercalibration in 2005-6 may be
incomplete due to - Monitoring systems not ready
- Insufficient biological monitoring data
- New assessment methods will evolve
- Monitoring systems of the new Member States need
to be harmonised
35Mission
- Scientific and technical platform for the
organisation of the intercalibration exercise(s).
- Harmonisation of the national ecological quality
assessment systems in EU and in Candidate
Countries