Short
summary
EUROHARP
includes nine
different
contemporary
methodologies for
quantifying
diffuse losses of
N and P, and a
total of 17 study
catchments across
gradients in
European climate,
soils, topography,
hydrology and land
use. These
methodologies have
been selected to
include those
approaches -
applicable at
catchment scale -
that are currently
used by European
research
institutes to
inform policy
makers at national
and international
levels.
Download
full version of
Description of
Work (DoW)
(.zip,
.doc)
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Objectives
The
first primary
objective of
EUROHARP is to
provide end-users
(national and
international
European
environmental
policy-makers)
with a thorough
scientific
evaluation of the
nine contemporary
quantification
tools and their
ability to
estimate diffuse
nutrient (N, P)
losses to surface
freshwater systems
and coastal
waters. Thereby
facilitate the
implementation of
the EC Water
Framework
Directive.
The
second primary
objective is to
develop an
electronic
decision support
system (tool-box)
for the
identification of
benchmarking
methodologies with
respect to both
costs and
benefits, for the
quantification of
diffuse nutrient
losses under
different
environmental
conditions across
Europe.
EUROHARP
will contribute
substantially to
improved
comparability,
transparency and
reliability of the
quantification of
nutrient losses
from diffuse
sources, and
thereby to
improved
efficiency of
abatement
strategies related
to the
implementation of
e.g. the Nitrates
Directive and the
Water Framework
Directive.
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Structure
The
work plan is
divided into six
work packages (WPs)
with the major
interconnections
between work
packages, as shown
in the figure.
Each Workpackage
is divided further
into tasks and
subtasks.
|
Interconnection diagram for the EUROHARP
project. The
arrows
indicate the direction of the main flow of
information/data/results.
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Workpackages
WP1:
Project Management
and Dissemination
The
project consortium
is well aware of
the complexity in
managing a project
involving nine
quantification
tools and 17
catchments in 17
European
countries.
Therefore, the
administrative and
scientific
management of the
project is
outlined in a
separate WP (WP1),
to allow a
transparent and
streamlined
project
management.
Furthermore, it
will facilitate a
continuous review
of resources and
costs linked to
project
management/co-ordination
and dissemination
throughout the
project period.
The
project co-ordinator
(PC) from NIVA-Norway
has the overall
responsibility and
the general
administrative
management of the
project. He will
also co-ordinate
WP1 and chair the
Annual Partner
meeting and the
Advisory Board
meetings. The five
other WPs have a
responsible from
each of five
different
institutes,
namely, EC-JRC-Italy,
ALTERRA-the
Netherlands, ADAS-UK,
NERI-
Denmark and
JORDFORSK-
Norway.
WP2:
Development of a
Catchment
Information System
WP2
focuses on the
collation and
management of
catchment data,
together with its
associated
quality, spatial
and temporal
resolution. WP2
collects the
necessary data
from all 17
catchments for use
by WPs 2, 3, 4, 5
and 6. The other
WPs will provide
feedback to WP2
throughout the
project period
whenever
additional data is
required.
WP3/WP4:
Application and
evaluation of
phosphorus (WP3)
and nitrogen
(WP4) loss
quantification
tools
The
intercomparison of
the
source-orientated
quantification
tools on three
core catchments
will be undertaken
in WP 3 (for
phosphorus) and WP
4 (for nitrogen).
The
intercomparison of
the quantification
tools for N and P
are separated into
two WPs because
the main processes
involved in
mobilisation and
transport within
and out from soil
differ between N
and P. Wherever
possible, resource
saving actions
will take place
between WP 3 and 4
e.g. by:
·
Setting up
(the parts of) the
quantification
tools requiring
comparable
parameterisation
data, such as soil
characteristics,
land use, climatic
parameters and
transfer
functions;
·
Setting up
the hydrological
representation in
some of the
quantification
tools;
·
Selecting
the sub-catchment
and/or specific
time period (3-5
years) for
calibrating each
quantification
tool;
·
Selecting
the specific time
period (3-5 years)
for testing the
performance for
each tool
(validation);
·
Developing
protocols with
criteria for
assessing model
performance; and
·
Organising
joint meetings
The
protocols
developed as
performance and
validation
criteria in WPs 3
and 4 will also be
used in WP 5
(application on
the 14 remaining
catchments) and WP
6 (scenario
analysis).
WP5:
Application of
methodologies to
analyse nutrient
pollution in a
European River Basin
Network
WP5
makes an
application and
validation of the
nine
quantification
tools on the 14
other catchments
(apart from the
three core
catchments already
studied in WP 3
and 4); based on
the European
harmonised data
sets prepared
under WP2.
QT9 (the
load orientated
quantification
tool) will be
applied on all 17
catchments.
The
main conclusions
drawn in WPs 3 and
4 will represent
an important input
when selecting the
combination matrix
of quantification
methodologies and
catchments in WP5.
Each of the source
orientated
quantification
tools will be
applied on at
least three
additional
catchments (out of
a total of 14)
where input data,
in general, is
more limited.
Within WP5, an
Export Group on
Retention in
surface waters
will quantify the
retention in
surface waters in
all the 17
catchments.
WP6:
Evaluation/synthesis
of model
performance and
river basin
Toolbox
The
result of the
performance,
validation
analyses and
inter-comparison
of the
quantification
tools on the three
catchments from
WP3 and WP4, and
the performance
and practicability
tests on the other
catchments within
WP5, will
represent the
input to the
synthesis and
overall
performance
evaluation and
cost-effectiveness
assessment
conducted in WP6.
The
main results from
WPs 3, 4 and 5
will represent
important inputs
to the toolbox to
be developed in
WP6. The toolbox
that will consist
of an inter-active
interface, will be
established based
on the outcome of
the activities
carried out in WPs
2-5 and task 6.3
in WP6. The
conceptual
framework of the
toolbox will be
developed based on
standard reporting
requirements
outlined in the
Water Framework
Directive, and any
relevant issues
from the HARP
Guidelines,
Barcelona
Convention and
HELCOM.
The
toolbox will be
developed to
assist various
end-users in
choosing an
appropriate
methodology to
assess the
environmental
pressure from
diffuse pollution
sources; by
quantifying
nutrient turnover
and surplus,
nutrient leaching
and loads,
including pathways
at different
scales and
temporal
resolutions, and
retention in
surface waters.
The toolbox will
guide the end-user
through different
steps that
introduce the
specific
methodologies,
their boundaries,
their demand for
input data, their
accuracy,
predictability and
their
cost-effectiveness,
and critical model
requirements.
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Advisory
Board
The
involvement of
‘end-users’ in
the EUROHARP
project is crucial
to obtain optimal
benefit of the
project
results/deliverables
for both the EC
and end-users at
the end of the
project period.
The Advisory Board
will be the major
channel for
discussing project
results and their
significance for
policy decisions
of end-user
organisations. The
Advisory Board
will meet once a
year.
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Organisational chart
showing decision
structures
(responsibilities)
for EUROHARP
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It
is important to
note that the
Advisory Board
will not be part
of the formal
decision-making
structure of
EUROHARP, but will
provide guidance
for the project
management (co-ordinator,
Steering
Committee), based
on end-user
interests.
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Models
EUROHARP
includes the
following nine
different
contemporary
methodologies for
quantifying
diffuse losses of
N and P:
|
Name
|
Modelling
Institute
|
Download
|
|
QT
1 -
NL-CAT
|
ALTERRA
(The
Netherlands)
|
.doc
|
|
QT
2 - REALTA
|
KMM
(Ireland)
|
.doc
|
|
QT
3 - N-LES
|
NERI
(Denmark)
|
.doc
|
|
QT
4 - MONERIS
|
FV-IGB
(Germany)
|
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QT
5 - TRK
(SOIL-N/HBV)
|
SLU,
SMHI
(Sweden)
|
.doc
|
|
QT
6 - SWAT
|
IRSA
(Italy)
|
.doc
|
|
QT
7 - EVENFLOW
|
ADAS
(United
Kingdom)
|
.doc
|
|
QT
8 - Nopolu
|
IFEN
(France)
|
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|
QT
9 - Source
Apportionment
|
NERI
( Denmark)
|
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