Ecological Modelling 265 (2013) 99–113
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Ecological Modelling
jo ur nal ho me page: www.elsevier.com/locate/ecolmodel
An advanced tool for eutrophication modeling in coastal lagoons:
Application to the Victoria lagoon in the north of Spain
Hala Zouiten
a,∗
, César Álvarez Díaz
a,b
, Andrés García Gómez
a,b
,
José Antonio Revilla Cortezón
a
, Javier García Alba
b
a
University of Cantabria, E.T.S.I. Caminos Canales y Puertos, Avda. de los Castros s/n, 39005 Santander, Spain
b
Environmental Hydraulics Institute “IH Cantabria”, C/Isabel Torres n
◦
15, Parque Científico y Tecnológico de Cantabria, 39011 Santander, Spain
a r t i c l e i n f o
Article history:
Received 21 November 2012
Received in revised form 31 May 2013
Accepted 4 June 2013
Keywords:
Eutrophication
Numerical model
Kinetics of phytoplankton
Kinetics of nutrients
Coastal lagoons
a b s t r a c t
A mathematical eutrophication model, EnvHydrEM (Environmental Hydraulics Institute Eutrophication
Model), was developed to be applied specifically to coastal lagoons. This model takes into consider-
ation 19 state variables, including phytoplankton, carbon (total inorganic carbon and sediment carbon),
phosphorus (organic phosphorus and phosphate), nitrogen (organic nitrogen, ammonia and nitrate), sil-
ica (available dissolved and particulate biogenic silica), dissolved oxygen, carbonaceous organic matter,
zooplankton, bacterioplankton, detritus, iron (total and ferrous iron) and manganese (total manganese
and manganous ion). EnvHydrEM also describes all possible interactions between the considered vari-
ables, showing biological and physicochemical processes that can occur in this type of aquatic systems.
These are usually characterized by a series of peculiar aspects which result mainly from the complex
interaction between inland and marine waters, as well as from a low hydrodynamic renewal rate. To
provide an example, the EnvHydrEM model was applied to the study of the eutrophication process in
the Victoria lagoon, in northern Spain. In this case study, the proposed model has proved its ability to
reproduce the chlorophyll-a concentration trends in the water body. The study also concluded that the
Victoria lagoon is a mesotrophic aquatic media in which silica is the most critical factor for the analysis
of its eutrophication state, due mainly to the presence of diatoms.
© 2013 Elsevier B.V. All rights reserved.
1. Introduction
Population growth and economic development, observed in
recent decades throughout the world, are the main factors respon-
sible for many of the environmental changes currently taking place.
These pressures greatly influence aquatic systems and are the result
of multiple human factors (urban, agricultural and industrial dis-
charges, sediment accumulation, modification of aquatic system
characteristics, etc.) which can cause a marked increase in the nutri-
ent inputs to the aquatic system. In several parts of the world,
this forced enrichment of nitrates (mainly from the agricultural
land washing), ammonia and phosphates (abundant in urban dis-
charges) has created an imbalance in aquatic systems known as
“cultural eutrophication”, manifested by a large algal production
and often followed by a decrease in dissolved oxygen, both of which
are harmful to wildlife (Carlson and Simpson, 1996; Rivera, 2002).
∗
Corresponding author. Tel.: +34 942201616x1144; fax: +34 942266361.
E-mail addresses: zouitenh@unican.es, h.zouiten@yahoo.fr (H. Zouiten),
alvarezc@unican.es (C.Á. Díaz), garciagan@unican.es (A.G. Gómez),
revillaj@unican.es (J.A.R. Cortezón), garciajav@unican.es (J.G. Alba).
Eutrophication can also have a natural origin, especially in sys-
tems with low hydrodynamic renewal. Traditionally the field of
limnology has used the terms eutrophic and oligotrophic environ-
ments to designate abundance or deficiency of organisms, organic
matter or nutrients. In this regard, eutrophic systems are those
in which the nutrient availability is able sustain a high biomass
and, conversely, pristine oligotrophic systems are those in which
the low availability of these substances limits the development of
biological activity. Originally, the terms eutrophic and oligotrophic
were used to describe the type of environments from a qualitative
point of view. Subsequently, other scales were developed based
on phytoplankton abundance in the system, in order to assess this
phenomenon from a quantitative approach. The scientific commu-
nity has since been accepted that the “eutrophic degree” of a water
body is quantified as the average annual concentration of chloro-
phyll in that environment (OCDE, 1982; Ryding and Rast, 1992).
Vollenweider (1976) was the first author who proposed measuring
the eutrophic degree of an ecosystem by means of the chlorophyll
concentration, a parameter which, in itself, is associated to the
increase in the water nutrient concentration.
Therefore, the evaluation of the trophic state of a water
body expresses the relationship between nutrient availability and
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http://dx.doi.org/10.1016/j.ecolmodel.2013.06.009