van Leeuwen et al.
eutrophic values for indicators of eutrophication across vast marine
zegions, while keeping a focus on local ecosystem functioning and
on the continuity of transboundary processes.
? Methcas
2.1 Ensemble method overview
Eight modelling centres participated in the ensemble modelling
exercise. To ensure comparable results between the different models
.n the ensemble, some harmonized model inputs were prescribed in
a joint protocol. These included all external sources of nutrients:
:iverine nutrient loads, atmospheric deposition and boundary
conditions. S imulation period and model output variables were
also prescribed. Meteorological forcing was not prescribed, to allow
the participants to use the same forcings as applied in published
validation results. Each partner also used its standard bathymetry,
‚or the same reason. Boundary conditions were taken from a shared
source. All partners were asked to submit results for 2009-2014 (the
COMP3 assessment period) for variables aligned with the
eutrophication assessment protocol by OSPAR: Dissolved
Inorganic Nitrogen (DIN, surface layer), Dissolved Inorganic
Phosphorus (DIP, surface layer), Total Nitrogen (TN, depth-
averaged), Total Phosphorous (TP, depth-averaged) and the
nitrogen to phosphorus (N:P, depth-averaged) ratio for the winter
period (December-February). Chlorophyll (Chl, surface layer),
chlorophyll 90’ percentile (Chl P90, surface layer) and light
attenuation (Ky, surface layer) were averaged over the growing
season (March-September), while near-bed oxygen levels (O,, near-
bed layer) and net primary production (netPP, depth-integrated)
were considered over the whole year. Models with no benthic
compartment applied a three-year spin up period to move from
10.3389/fmars.2023.1129951
initial conditions. Models with a benthic compartment capable of
nutrient storage applied a longer, suitable spin up period for the
historic scenario to arrive at an equilibrium between benthic
nutrients and the applied nutrient inputs.
The participating modelling centres were: the Cefas (Centre for
Fisheries and Aquaculture Science, Lowestoft, UK), Deltares
(Netherlands), IFREMER (L’Institut Francais de Recherche pour
V’Exploitation de la Mer, France), JRC (Joint Research Centre in
[spra, Italy but representing the EU), the University of Oldenburg
(Oldenburg, Germany), RBINS (Royal Belgian Institute of Natural
Sciences, Belgium), SMHI (Swedish Meteorological and
Hydrological Institute, Sweden), and the University of Hamburg
together with the Helmholtz Zentrum Geesthacht (now called
Hereon) (UHH-HZG, Germany). A detailed overview of the
different models is provided in Appendix D (descriptions,
Supplementary Materials) and E (table overview, Supplementary
Materials). Both large domain models (covering the entire
Northwest European shelf) and small domain models (covering
2.g. only the English Channel or the Southern North Sea) were
applied to the exercise.
The different models have varying degrees of complexity with
respect to the processes they represent. Not all use the same external
nutrient inputs (Table 1) or have the same number of plankton
functional groups (Appendix E; Supplementary Table 2). Besides
internal model differences the simulations used in this exercise also
differ in spatial resolution (Appendix E; Supplementary Table 2)
and coverage (Figure 1). Only the SMHI model domain includes the
“ull Baltic Sea, all other domains have an open boundary with the
Baltic in the Belt Sea region. Table 1 shows the nutrients that are
used as inputs in the different models. Note that even if a model
does not use input for a certain nutrient, the dynamics of this
nutrient are usually still part of the model’s internal dynamics
(Appendix E; Supplementary Table 2).
TABLE 1 Overview of the nutrients used by each model from the supplied riverine inpı.*
MIRO&CO | RBINS (BE)
MARS3D-
Ifremer (FR)
MANGA4
X
X:
Uni-Hamburg
ECOHAM
/HZG (DE)
GPM | Uni-Oldenburg
(DE)
DFLOW-FW Deltares (NL)
GETM-JRC-
) JRC (ZU)
ERSEM
GETM-ERSEM-
Cefas (UK) l
BFM
NEMO-SCOBI SMHI (SE) | x
BY) mm
Aere “Uni” stands for “University of”. Q stands for fresh water discharge
"rontiers in Marine 1cience
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