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  <front>
    <journal-meta />
    <article-meta>
      <title-group>
        <article-title>The Influence of Climatic-oceanographic Changes in Aquaculture. A Case Review Concerning Mussel Farming from Vistonikos Bay, Greece</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Ioannis Georgoulis</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Ioannis A. Giantsis</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Athanasios Lattos</string-name>
          <email>aqualattos@gmail.com</email>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Vassilios Pisinaras</string-name>
          <email>v.pisinaras@swri.gr</email>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Konstantinos Feidantsis</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Basile Michaelidis</string-name>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Georgios A. Delis</string-name>
          <email>delis@vet.auth.gr</email>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Alexandros Theodoridis</string-name>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>Department of Animal Science, Faculty of Agricultural Sciences, University of Western Macedonia</institution>
          ,
          <addr-line>53100 Florina</addr-line>
          ,
          <country country="GR">Greece</country>
        </aff>
        <aff id="aff1">
          <label>1</label>
          <institution>Laboratory of Animal Physiology, School of Biology, Aristotle University of Thessaloniki</institution>
          ,
          <addr-line>54124 Thessaloniki</addr-line>
          ,
          <country country="GR">Greece</country>
        </aff>
        <aff id="aff2">
          <label>2</label>
          <institution>School of Veterinary Medicine, Faculty of Health Sciences, Aristotle University of Thessaloniki</institution>
          ,
          <addr-line>54124 Thessaloniki</addr-line>
          ,
          <country country="GR">Greece</country>
        </aff>
        <aff id="aff3">
          <label>3</label>
          <institution>Soil and Water Resources Institute, Hellenic Agricultural Organization “Demeter”</institution>
          ,
          <addr-line>57400</addr-line>
        </aff>
      </contrib-group>
      <fpage>51</fpage>
      <lpage>61</lpage>
      <abstract>
        <p>Mussel farming in Vistonikos Bay, North Aegean, constitutes an activity of high socio-economic importance. The wide area consists of three basins rich in organic material, namely Porto Lagos Lagoon, Vistonicos Gulf and Vistonida lake. Oceanographic morphology, sea currents, meteorological and climatic conditions, as well as the primary productivity of the wide marine area of Vistonikos Bay, favor mussel farming development but sometimes may affect them harmfully. In the present review, historical oceanographic and meteorological data are discussed, including seawater temperature, air temperature, monthly rainfall and wind dynamics, in an aquaculture related point of view. Supporting evidence revealed that occasional restrictions imposed to mussel farm units in the past are related to climatic factor extremes. However, overall, Vistonikos Bay demonstrates a suitable area for maintenance and further development of aquaculture of mussels and other bivalves.</p>
      </abstract>
      <kwd-group>
        <kwd>Mussel farming</kwd>
        <kwd>temperature</kwd>
        <kwd>Vistonikos</kwd>
        <kwd>wetland</kwd>
        <kwd>Aegean Sea</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>1 Introduction</title>
      <p>
        The wetland area of Vistonikos Bay - Porto Lagos Lagoon - Vistonida Lake
extends between the Prefecture of Xanthi to the west and Rodopi to the east (Figure
1). Specifically, Porto Lagos Lagoon is located in the center of these three reservoirs
and is connected to the north with Vistonida Lake through three canals and to
southwest with Vistonikos Bay through one canal
        <xref ref-type="bibr" rid="ref10">(Koutrakis et al., 2005)</xref>
        . Vistonida
Lake receives to its northern part, the freshwater inflow from Kosynthos, Kompsatos
and Travos streams
        <xref ref-type="bibr" rid="ref19">(Tsakoumis et al., 2016)</xref>
        , enriching the lake with significant
amounts of nutrients of agricultural origin, as well as processing of domestic and
industrial waste water
        <xref ref-type="bibr" rid="ref12">(Markou et al., 2006)</xref>
        , whereas its southern part is of higher
salinity due to the entering seawater
        <xref ref-type="bibr" rid="ref10">(Koutrakis et al., 2005)</xref>
        .
      </p>
      <p>
        The three reservoirs of Porto Lagos Lagoon, Vistonicos Bay and Vistonida Lake
are characterized as small average depth, 2-3, 8 and 2 meters respectively
        <xref ref-type="bibr" rid="ref10 ref12">(Koutrakis
et al., 2005; Markou et al., 2006)</xref>
        . Combined with the shallow depth, the tidal
conditions of the area favor the development of all forms of fishing activities,
including aquaculture. Furthermore, the ripple effect is negligible in the lagoon and
very small on the east side of the Vistonicos Bay, near Fanari area, where mussel
aquacultures are located, while the continuous circulation of water due to the
presence of canals and benthic morphology constitute the major factors for sufficient
water oxygenation
        <xref ref-type="bibr" rid="ref4">(Dimiza et al, 2016)</xref>
        .
      </p>
      <p>
        The wide area is also a habitat of high ecological importance, which contributes to
the numerous meadows of Posidonia and other aquatic plants, forming in many
places an environment suitable for a habitat of oyster and other bivalve’s offspring
and juvenile fish. The whole habitat is also recognized as part of the National Park of
Eastern Macedonia and Thrace, which is one of the 10 Greek wetlands protected by
the Ramsar Convention and also as a protected area included in the European Union's
Natura 2000 network
        <xref ref-type="bibr" rid="ref4">(Dimiza et al., 2016)</xref>
        .
      </p>
      <p>The Vistonikos-Porto Lagos wetland exhibits an enormous fishing value at
primary production levels. Fisheries have been for many decades a very important
activity for Vistonicos, which in combination with the rest Thracian sea,
Strymonikos Gulf, Kavala Bay and coasts of Thasos, accounts for more than 30% of
the country's marine catches that are landed and traded (ELSAT, 2018).</p>
      <p>
        Mussel farming was first developed in the region in 1999, when seven mussel
farm units were environmentally and administratively licensed (Decisions DAMT
654-656/24-10-2000, 633/1-11-2001, 640/1-11-2001) (Figure 1). Given the
recognition and protection of the area through the Ramsar and Natura 2000
Convention, this form of aquaculture is a fully compliant activity with these
regulations as well as with the protection of the natural environment, since the
burden on the marine area is negligible and derives solely from secretions of farmed
mussels
        <xref ref-type="bibr" rid="ref5">(Eleftheriadis, 2001)</xref>
        . It should be also noted that the first units started with
native mussel populations from the area itself, thereby avoiding biological
contamination with alien species and at the same time stimulating the local shellfish.
In the present review, historical oceanographic and meteorological data are
discussed, including seawater temperature, air temperature, monthly rainfall and
wind dynamics, in an aquaculture related point of view.
      </p>
    </sec>
    <sec id="sec-2">
      <title>2 Area properties</title>
      <sec id="sec-2-1">
        <title>2.1 Oceanography</title>
        <p>
          The Aegean Sea archipelago is characterized by various seabed topologies,
encompassing many differential depth and relief areas. In contrast, the Vistonikos
Bay exhibits a greater uniformity with lower depths
          <xref ref-type="bibr" rid="ref1">(Androulidakis et al., 2017)</xref>
          . The
larger part of Vistonikos seabed is sandy, hosting many coastal areas with Posidonia
meadows, while rocky areas are fewer
          <xref ref-type="bibr" rid="ref4">(Dimiza et al., 2016)</xref>
          . At Fanari Cape, an
artificial reef system was constructed and installed in 1999, consisting of a protective
zone (240 m3) and a core (9 Italian and 9 French artificial reefs) exceeding length of
6 km at an approximate depth of 25 km
          <xref ref-type="bibr" rid="ref11">(Manoudis et al., 2005)</xref>
          . The construction of
these artificial reefs is a measure of great importance for the management of coastal
marine ecosystems and has also proven to be very effective in enhancing fisheries
          <xref ref-type="bibr" rid="ref15">(Pickering et al., 1998)</xref>
          . They can also play an important role in the marine area of
the coastal zone, including protection against the mechanical impacts of fishing gear,
such as trawling, habitat restoration, increased territorial heterogeneity and substrate
diversity in deep seabirds
          <xref ref-type="bibr" rid="ref11">(Manoudis et al, 2005)</xref>
          .
        </p>
      </sec>
      <sec id="sec-2-2">
        <title>2.2 Sea currents</title>
        <p>
          The mechanisms of water circulation depend on the amount of water and other
hydrological factors, such as wind intensity, thermal fluxes, salinity flows and
upstream movement due to river outflows. In the North Aegean the circulation of
water is cyclonic (Figure 2). The flow of the North Aegean streams is strongly
influenced by the outflow from the Black Sea and the additional influx of fresh water
from rivers. These inflows are low salinity and are offset by an influx of more saline
waters from the eastern Mediterranean that balance the salinity of the Aegean in
general
          <xref ref-type="bibr" rid="ref16">(Poulos et al., 1997)</xref>
          . In particular, the salinity of the Black Sea waters is
lower (29.6‰) than the corresponding Aegean waters (38,9‰), therefore they are
lighter and move superficially in the water column. On the contrary, the waters of the
Aegean flow to the bottom of the water column heading towards the Black Sea,
forming a countercurrent stream. However, it should be noted that the low salinity
water outflow from the Dardanelles is the most important lateral buoyancy force,
which exceeds that of all rivers
          <xref ref-type="bibr" rid="ref9">(Kourafalou and Barbopoulos, 2003)</xref>
          . These streams
have lower temperature and higher nutrient content than the oligotrophic Aeagean
          <xref ref-type="bibr" rid="ref17">(Siokou-Frangou et al., 2002)</xref>
          , which favored the development of mussel aquaculture
in the Aegean northern parts, such as Thermaikos, Vistonikos and the bay of Kavala.
In particular, in the region of Vistonikos, recorded salinity values are considered
normal for coastal waters near estuaries. The lowest values are found in the surface
layers of the water column (0 - 4 meters deep). Also, lower salinity values are usually
observed during the winter. The transfer of fresh water from lake Vistonida
contributes to these lower salinity values as well.
        </p>
        <p>
          The precise determination of the hydrodynamic circulation in the Vistonicos Bay
presents many difficulties. The currents depend on many causes, most notably winds,
tides and densities
          <xref ref-type="bibr" rid="ref11">(Manoudis et al., 2005)</xref>
          . The tidal effect within the Vistonikos
Bay is generally low, however it plays an important role in the rotation of the
maritime masses, but also, in conjunction with underground currents, in the
transporting of pollution outward to the bay. Density differences play an important
role in the local movement of water (surface - bottom). They occur mainly during the
hot season when the surface layers of water are heated, thus becoming lighter than
the deeper layers. As a result, there is a lack of oxygenation of the deeper marine
masses. On the contrary, during the winter season, the surface layers of water get
cooler, become heavier and sink, disturbing water stratification, thus homogenizing
the water column and helping the oxygenation of water throughout the column. This
is particularly important for the survival of mussels, which are susceptible to low
concentrations of dissolved oxygen
          <xref ref-type="bibr" rid="ref2">(Anestis et al., 2007)</xref>
          , whereas the general
cyclonic water flow of the North Aegean is, among other factors, responsible for the
genetic homogeneity of the mussel populations
          <xref ref-type="bibr" rid="ref7">(Giantsis et al. 2014)</xref>
          . Although
winds are the main cause of water circulation, they are of variable direction and
intensity on a small-time scale. Therefore, currents also follow this variable state.
The prevailing winds are the northeast, from which mussel cultivation units are
protected. Surface currents are correlated with the direction of the winds, while the
deeper currents have usually an opposite direction.
2.3
        </p>
      </sec>
      <sec id="sec-2-3">
        <title>Meteorological and climatic data</title>
        <p>The climate of Eastern Macedonia – Thrace is generally typical Mediterranean
with mild winters and a dry, warm summer. During winter the general circulation of
the atmosphere brings to the region winds of western origin, which are closely linked
to cyclonic crossings and polar air intrusions. Also, winter months are mostly rainy,
due to the meet up of tropical warm winds with polar cold winds, and they have more
than twice of the average rainfall over the rest of the months (Figure 3).</p>
        <p>
          In contrast, during summer, northern winds weaken locally due to the action of the
sea breeze. While the mean monthly air temperature during summer does not exceed
26 °C, instant daily temperature often reaches 40 °C (Figure 4). The average seasonal
temperature range is between 15 °C and 26 °C in surface waters in the Aegean
(Figure 5) and can adversely affect mussel survival during summer months,
occasionally causing direct mortality to mussels, increase of harmful microorganism
populations and reduce of dissolved oxygen availability. The maximum critical
temperature limit of Mytilus galloprovincialis mussels depends on the residence time
and has been calculated at 28 °C for a few days or at 26 °C for a period of 2 weeks
          <xref ref-type="bibr" rid="ref13">(Mavridou et al, 2016)</xref>
          .
        </p>
      </sec>
      <sec id="sec-2-4">
        <title>2.4 Primary productivity</title>
        <p>
          Primary marine productivity is defined as the production of chlorophyll
phytoplankton
          <xref ref-type="bibr" rid="ref18">(Smetacek et al., 2002)</xref>
          , a property of great importance for the
development of mussels. These organisms synthesize, via photosynthesis, organic
compounds from inorganic salts dissolved in seawater, like nitrogen, phosphoric and
silicon salts, and carbon dioxide. These nutrient inorganic salts represent higher
concentrations in coastal waters and estuaries as well as at high depths. Also, these
concentrations are even higher during winter season, due to the mixing of water
column, and in mid-autumn when the thermal sea water column is completed.
        </p>
        <p>
          Usually nitrogen and phosphoric salts in the seas are limiting factors for the
production of biomass (primary production). On the other hand, silicon does not
appear to be a limiting factor except for diatoms
          <xref ref-type="bibr" rid="ref18">(Smetacek et al, 2002)</xref>
          .
        </p>
        <p>
          In Vistonikos Bay the concentrations of orthophosphate range from zero, during
summer season, to the highest concentrations of 75.1 μg/l
          <xref ref-type="bibr" rid="ref5">(Eleftheriadis, 2001)</xref>
          ,
which are observed from the end of winter to the middle of spring. As for nitrates
concentrations, they represent the highest values during winter, and they drop during
summer (less than 10 μg/l). Also, the concentrations of ammonium salts are higher
than those of nitrate and nitrite, with the highest values being observed during winter,
as well as in spring. All these above values of inorganic salts can be characterized as
suitable for aquaculture, providing ideal nutritional conditions for the growth of
mussels.
3 The effect of meteorological-climatic data on mussel farming in
Vistonikos Bay
        </p>
        <p>The reasons that contributed to the development of mussel aquaculture in
Vistonikos Bay can be summarized (a) in the presence of natural shellfish
populations, (b) in the quality of water in combination with the sea currents and
shoreline morphology and (c) the presence of the Porto Lagos port and the Fanari
fishing harbor.</p>
        <p>
          However, in 2010, the production of “all mussels” in the area was completely
destroyed due to the emergence of phytoplankton. The high concentrations of toxic
phytoplankton in seawater occurred at the end of summer and early autumn, periods
when the highest temperatures were observed (Figure 4). Also, in 2012, a series of
unexplained deaths in experimental mice were observed, that were attributed to
lipophilic toxins with nerve symptomatology
          <xref ref-type="bibr" rid="ref20">(Vlamis et al., 2015)</xref>
          . Increased
concentrations of harmful microorganisms, such as toxic phytoplankton and
toxinsecreting bacteria, are positively correlated with high temperatures (Jay, 2000). Such
problems can be avoided in mussel aquaculture by monitoring the physicochemical
properties of seawater and the early collection or transport of cultivated populations
during periods of increased risk.
        </p>
        <p>
          Generally, near heat stress limits, mussels show a decrease in aerobic capacity.
This decrease is not necessarily caused by the decrease in ambient oxygen levels, but
mainly by the limited capacity of oxygen delivery mechanisms, such as the exchange
of gases with the surrounding environment
          <xref ref-type="bibr" rid="ref2">(Anestis et al., 2007)</xref>
          .
        </p>
        <p>Mussel aquaculture is a particularly lucrative form of primary production in
Greece. The oceanographic characteristics, the water physicochemical properties, the
meteorological and climatological data of Vistonikos Bay and Porto Lagos, as
summarized above, demonstrate the suitability of the area for the development of the
aquaculture. However, occasionally, as marked in 2010-2012, production may be
influenced by secondary factors that are directly dependent on the climate. Therefore,
accurate monitoring of the temperature and physicochemical characteristics of
seawater in mussel farms may be a valuable solution to such kind of problems and
limitations and contribute as new tools for the rational management of mussel
aquaculture.</p>
        <p>Acknowledgement. This research has been co-financed by the European Union and
Greek national funds through the Operational Program Competitiveness,
Entrepreneurship and Innovation, under the call Special Actions AQUACULTURE –
INDUSTRIAL MATERIALS – OPEN INNOVATION IN CULTURE (project code:
T6YBΠ-00388; Project acronym: SmartMussel).
eastern Mediterranean: genetic panmixia in the Aegean and the Ionian Seas.
Journal of the Marine Biological Association of the United Kingdom, 94, 797–
809.</p>
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