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1 Hellenic Centre for Marine Research (HCMR) Institute of Oceanography 46.7 km Athens-Sounio Avenue 19013 Anavyssos, Greece E-mail: [email protected] 1 1 2 2 1 1 A.P. Karageorgis , D. Georgopoulos , V. Karathanassi , S. Ioannidou , V. Papadopoulos , C. Tsabaris 1 1 2 2 1 1 A.P. Karageorgis , D. Georgopoulos , V. Karathanassi , S. Ioannidou , V. Papadopoulos , C. Tsabaris Surficial and submarine freshwater discharges in a tidal Mediterranean embayment: hydrology and seawater optical characteristics Surficial and submarine freshwater discharges in a tidal Mediterranean embayment: hydrology and seawater optical characteristics INTRODUCTION Freshwater, groundwater and coastal seawater interactions have received considerable attention during the past decade, due to increasing interest regarding basin-scale inputs into the coastal zone. Submarine groundwater discharges (SGD) have been studied in the last few years only, as important pathways of freshwater, nutrients, and other inorganic and organic substances into the sea. Here we present information from the nationaly funded project ‘IRIS’ regarding the influence of freshwater inputs from coastal springs and SGD on: (1) temperature, salinity, chlorophyll-a, and particulate matter, and (2) optical seawater characteristics, as well as, the spatial and temporal distribution fields of the aforementioned parameters. - th 40 Annual Congress of the Canadian Meteorological and Oceanographic Society CMOS: 29 May-1 June 2006, Toronto Canada th 40 Annual Congress of the Canadian Meteorological and Oceanographic Society CMOS: 29 May-1 June 2006, Toronto Canada REGIONAL SETTING The study area (Agios Stefanos Bay) is situated at the northern sector of south Evvoikos Gulf, in central Greece (eastern Mediterranean Sea); it is an area well-known for its strong tidal currents (Euripus Strait) and the recently identified SGD (Fig. 1). RESULTS AND DISCUSSION The results revealed that the inflow of surficial and submarine freshwater (brackish, salinity 6-7 psu) discharges affected substantially the horizontal distribution of the parameters measured in terms of: (1) -1 lower temperature (min 14.7 °C); (2) lower salinity (min 28.3 psu); (3) high PMC (max 8.5 mg l ); and (4) -1 high chlorophyll-a concentration (max 3 g l ) (Figs 2, 3). Freshwater flowing along the coast from small sub-aerial springs was distributed over the area as a thin surficial film (~1 cm), with decreasing trend as the distance from the sources increased. By contrast, SGD appeared as permanent gyres of a 3-5 m diameter, which were visible clearly by bare eye (Fig. 4); increased turbulence and rapid mixing was a major characteristic observed, resulting in high PMCs. Probably this environment favors mussel growth on the seabed (Figs. 5, 6). Moreover, processing of radiance and reflectance data revealed the most appropriate wavelengths for the spectral detection of the SGD (488.20-573.33 and 552.85-769.70 nm for radiance and reflectance, respectively). In addition, the evaluation of groundwater pathways and fluxes into the coastal zone can be made with the 222 use of natural tracers. Rn is an excellent tracer due to its large enrichment in SGD, unreactive nature and short half life (3.83 days). So, a test measurement has been performed with a submarine gamma-ray detector (K-A-TE-RINA) at the same study area. Preliminary results provide significant information about the radon 222 214 214 concentration (Bq/m3) detected by the gamma ray emission of Rn daughters ( Bi and Pb), which appears to be highly enriched in SGD (Fig. 8).. Preliminary results obtained from the airborne sensor TABI revealed clearly the plume of cold surficial freshwater inputs (Fig. 7). 2 Laboratory of Remote Sensing National Technical University of Athens 9 Heroon Polytechniou 15780 Athens, Greece E-mail: [email protected] National Technical University of Athens Athens Figure 1. Study area location map (Google Earth) and sampling stations (yellow rhombs) occupied during June 2005. Submarine groundwater discharge points are illustrated in red arrows. GREECE e I nian a o S Mediterranean Sea Aegean Sea METHODS Oceanographic measurements were conducted during April 2005 and June 2005, using standard field equipment (portable SeaBird CTD with transmissometer and optical backscatter sensors, and GER 1500 radiometer). Water samples were used for the determination of particulate matter (PMC) and chlorophyll-a concentrations; the Radiance and reflectance of surface seawater was also measured. salinity of the upper 1-cm seawater was determined by a salinometer. Figure 2. Spatial distribution of temperature (left) and salinity (right) at the surface waters of Agios Stefanos Bay, during June 2005. Figure 3. Spatial distribution of particulate matter concentration (left) and chlorophyll-a concentration (right) at the surface waters of Agios Stefanos Bay during June 2005, and April 2005, respectively. Session O5: Coastal Oceanography and Inland Waters, Abstract No. 776 Session O5: Coastal Oceanography and Inland Waters, Abstract No. 776 Figure 4. Turbulent gyres generated by SGD at the eastern sector of Agios Stefanos Bay in south Evvoikos Gulf. These features are characterized by lower temperature and salinity, and higher particulate matter and chlorophyll-a concentrations than the ambient seawaters. Hellenic Centre for Marine Research Institute of Oceanography Figure 5. A local fisherman digs the shallow muddy seabed to collect mussels, into the area where fresh spring water and submarine groundwater discharge. Figure 6. The seabed near the freshwater discharge sector was generally muddy and mussel beds were abundant. Sediment resuspension due to high turbulence was intense and visibility was very low. Channels 0 200 400 600 800 1000 counts 10 0 10 1 10 2 10 3 10 4 10 5 222 Rn results: measured activity: 1450 Bq/m 3 activity at open sea: 3-5 Bq/m3 3 214 Bi (daughter of 222 Rn) 40 K 214 Bi (daughter of 222 Rn) Figure 8. In-situ test for SGD using the K-A-TE-RINA underwater detector. Figure 7. Image acquired with the airborne thermal sensor TABI (8-12 ìm) during June 2005. The freshwater plume is identified by its darker color, indicating lower sea surface temperature. Counts

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Page 1: Surficial and submarine freshwater discharges in a tidal ...portal.survey.ntua.gr/geohopper/iCommons/ePubl_VKarath/CMOS_co… · short half life (3.83 days). So, a test measurement

1Hellenic Centre for Marine Research (HCMR)Institute of Oceanography46.7 km Athens-Sounio Avenue19013 Anavyssos, GreeceE-mail: [email protected]

1 1 2 2 1 1A.P. Karageorgis , D. Georgopoulos , V. Karathanassi , S. Ioannidou , V. Papadopoulos , C. Tsabaris1 1 2 2 1 1A.P. Karageorgis , D. Georgopoulos , V. Karathanassi , S. Ioannidou , V. Papadopoulos , C. Tsabaris

Surficial and submarine freshwater discharges in a tidal Mediterranean embayment: hydrology and seawater optical characteristics

Surficial and submarine freshwater discharges in a tidal Mediterranean embayment: hydrology and seawater optical characteristics

INTRODUCTIONFreshwater, groundwater and coastal seawater interactions have received considerable attention during the past decade, due to increasing interest regarding basin-scale inputs into the coastal zone. Submarine groundwater discharges (SGD) have been studied in the last few years only, as important pathways of freshwater, nutrients, and other inorganic and organic substances into the sea. Here we present information from the nationaly funded project ‘IRIS’ regarding the influence of freshwater inputs from coastal springs and SGD on: (1) temperature, salinity, chlorophyll-a, and particulate matter, and (2) optical seawater characteristics, as well as, the spatial and temporal distribution fields of the aforementioned parameters.

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REGIONAL SETTINGThe study area (Agios Stefanos Bay) is situated at the northern sector of south Evvoikos Gulf, in central Greece (eastern Mediterranean Sea); it is an area well-known for its strong tidal currents (Euripus Strait) and the recently identified SGD (Fig. 1).

RESULTS AND DISCUSSIONThe results revealed that the inflow of surficial and submarine freshwater (brackish, salinity 6-7 psu) discharges affected substantially the horizontal distribution of the parameters measured in terms of: (1)

-1lower temperature (min 14.7 °C); (2) lower salinity (min 28.3 psu); (3) high PMC (max 8.5 mg l ); and (4) -1high chlorophyll-a concentration (max 3 g l ) (Figs 2, 3). Freshwater flowing along the coast from small

sub-aerial springs was distributed over the area as a thin surficial film (~1 cm), with decreasing trend as the distance from the sources increased. By contrast, SGD appeared as permanent gyres of a 3-5 m diameter, which were visible clearly by bare eye (Fig. 4); increased turbulence and rapid mixing was a major characteristic observed, resulting in high PMCs. Probably this environment favors mussel growth on the seabed (Figs. 5, 6).Moreover, processing of radiance and reflectance data revealed the most appropriate wavelengths for the spectral detection of the SGD (488.20-573.33 and 552.85-769.70 nm for radiance and reflectance, respectively).

In addition, the evaluation of groundwater pathways and fluxes into the coastal zone can be made with the 222use of natural tracers. Rn is an excellent tracer due to its large enrichment in SGD, unreactive nature and

short half life (3.83 days). So, a test measurement has been performed with a submarine gamma-ray detector (K-A-TE-RINA) at the same study area. Preliminary results provide significant information about the radon

222 214 214concentration (Bq/m3) detected by the gamma ray emission of Rn daughters ( Bi and Pb), which appears to be highly enriched in SGD (Fig. 8)..

Preliminary results obtained from the airborne sensor TABI revealed clearly the plume of cold surficial freshwater inputs (Fig. 7).

2Laboratory of Remote SensingNational Technical University of Athens9 Heroon Polytechniou15780 Athens, GreeceE-mail: [email protected]

National Technical

University of Athens

Athens

Figure 1. Study area location map (Google Earth) and sampling

stations (yellow rhombs) occupied during June

2005. Submarine groundwater discharge points are illustrated in

red arrows.

GREECE

e

Inian

a

oS

Mediterranean Sea

AegeanSea

METHODSOceanographic measurements were conducted during April 2005 and June 2005, using standard field equipment (portable SeaBird CTD with transmissometer and optical backscatter sensors, and GER 1500 radiometer). Water samples were used for the determination of particulate matter (PMC) and chlorophyll-a concentrations; the

Radiance and reflectance of surface seawater was also measured.

salinity of the upper 1-cm seawater was determined by a salinometer.

Figure 2. Spatial distribution of temperature (left) and salinity (right) at the surface waters of Agios Stefanos Bay, during June 2005.

Figure 3. Spatial distribution of particulate matter concentration (left) and chlorophyll-a concentration (right) at the surface waters of Agios Stefanos Bay

during June 2005, and April 2005, respectively.

Session O5: Coastal Oceanography and Inland Waters, Abstract No. 776Session O5: Coastal Oceanography and Inland Waters, Abstract No. 776

Figure 4. Turbulent gyres generated by SGD at the eastern sector of Agios

Stefanos Bay in south Evvoikos Gulf. These features are characterized by lower temperature and salinity, and

higher particulate matter and chlorophyll-a concentrations than the

ambient seawaters.

Hellenic Centre for

Marine Research

Institute of Oceanography

Figure 5. A local fisherman digs the shallow muddy seabed to collect mussels, into the area where fresh

spring water and submarine groundwater discharge.

Figure 6. The seabed near the freshwater discharge sector was

generally muddy and mussel beds were abundant. Sediment resuspension due

to high turbulence was intense and visibility was very low.

In situ test for submarine groundwater discharge by using the K-A-TE-RINA underwater detector

Channels

0 200 400 600 800 1000

co

un

ts

100

101

102

103

104

105

222Rn results: measured activity: 1450 Bq/m

3

activity at open sea: 3-5 Bq/m33

214

Bi(daughter of

222Rn)

40K

214

Bi(daughter of

222Rn)

Figure 8. In-situ test for SGD using the K-A-TE-RINA underwater

detector.

Figure 7. Image acquired with the airborne thermal sensor TABI (8-12

ìm) during June 2005. The freshwater plume is identified by its

darker color, indicating lower sea surface temperature.

Co

un

ts