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North Aegean Sea Kostas Tsiaras, Chris Smith, George ... - meece

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<strong>North</strong> <strong>Aegean</strong> <strong>Sea</strong><br />

<strong>Kostas</strong> <strong>Tsiaras</strong>, <strong>Chris</strong> <strong>Smith</strong>, <strong>George</strong> Petihakis,<br />

<strong>George</strong> Triantafyllou<br />

H.C.M.R<br />

Scenario definition Workshop<br />

Bologna, June 2010


N. <strong>Aegean</strong> Coupled model<br />

Hydrodynamic model: POM (Blumberg and Mellor, 1983)<br />

Biogeochemical model: ERSEM-II (Baretta et al., 1995)<br />

POC<br />

DOC<br />

N, P, Si<br />

PicoPhyto Flagellates<br />

NanoPhyto Diatoms<br />

Bacteria<br />

Heterotr.<br />

Flagellates<br />

Microzoo<br />

Pelagic Model<br />

Mesozoo<br />

Si<br />

CO 2<br />

NO 3<br />

PO 4 NH4<br />

Sedimentation<br />

Benthic Model


Hindcast simulation 1985-2007 (spin-up 1980-1985)<br />

Atm. Forcing: 1980-2001 ERA40 Downscaled (0.5 o x 0.5 o ), Hermann and Somot, 2008<br />

2000-2008 HCMR POSEIDON operational (6-hour, 1/10)<br />

Rivers: Q, NO3, PO4 from SESAME, Ludwig et al. 2009, Dumont et al., 2005<br />

Initial Condition: NO3, PO4 from Medatlas 2002 climatology +spin-up<br />

Open sea productivity<br />

~ vertical mixing variability<br />

+ net nutrient flux across boundary<br />

-Dense water formation events (EMT)<br />

-SST increase around 1998 (~0.7 o C)


Climatic time-slice simulations 1990-2000 & 2090-2100 (A1B)<br />

to be extended to 20 years (1980-2000 & 2080-2100)<br />

Atm. Forcing: INGV-SXG (A1B, 1.2 o x 1.2 o ), Scoccimarro, 2007<br />

to be compared with IPSL forcing<br />

Rivers: Q, NO3, PO4 from SESAME (A1B scenario),<br />

Ludwig et al. 2009, Dumont et al., 2005<br />

Initial Condition: from hindcast simulation<br />

Increase in SST (~1 o C) +similar SSS<br />

increased stratification<br />

decrease in River discharge (~46%)<br />

+increase in nutrients concentrations -><br />

~similar nutrient river load (~8% decrease)<br />

weak productivity decrease in<br />

open sea (1%) and<br />

river influenced areas (3%)


Implementation of Acidification module<br />

-Setup of Mediterranean carbonate system model and preliminary simulations<br />

-Validation against DYFAMED and SESAME data<br />

-further calibration/validation in progress<br />

DYFAMED data SESAME data<br />

Begovic et al., 2002<br />

Krasakopoulou et al., submitted


Biomass (tonnes)<br />

ERSEM-POM coupling with OSMOSE<br />

Coupling Setup done<br />

Mapping of the area,<br />

Link of LTL model (ERSEM) with OSMOSE (7 phyto-zooplankton groups)<br />

Test case with 3 key species (anchovy, sardine, Scomber japonicus)<br />

140000<br />

120000<br />

100000<br />

80000<br />

60000<br />

40000<br />

20000<br />

0<br />

1 3 5 7 9 11<br />

Year<br />

13 15 17 19<br />

Anchovy<br />

Sardine<br />

In progress<br />

-setup of genetic algorithm to calibrate OSMOSE<br />

-finalize parameter set for all N. <strong>Aegean</strong> species<br />

Chub Mackeler Species Landings (Kg) % A<br />

Engraulis engrasicolus 23,502,489 43.7<br />

Sardina pilchardus 13,221,956 24.6<br />

Merluccius merluccius 4,406,099 8.2<br />

Boops boops 2,708,538 5.0<br />

Scomber japonicus 2,706,409 5.0<br />

Trachurus sp. 1,548,909 2.9<br />

Spicara smaris 1,149,183 2.1<br />

Scomber scombrus 1,137,496 2.1<br />

Sarda sarda 999,290 1.9<br />

Total 53,734,618


Fisheries<br />

Coupled ERSEM-OSMOSE model - possible fishing scenarios:<br />

1) Equilibrium (no change, constant harvesting of species)<br />

2) Different changes in effort (Fishing days, No. of boats)<br />

3) Change in closed fishing areas (geographical or depth related)<br />

4) Change in closed fishing seasons (Purse seines, trawlers)<br />

5) Fisheries pressure on specified species<br />

Species Fishing Gear Open <strong>Sea</strong>son<br />

Engraulis engrasicolus Purse seine 1 Mar - 15 Dec<br />

Sardina pilchardus Purse seine 1 Mar - 15 Dec<br />

Merluccius merluccius Trawl 1 Oct - 30 May<br />

Boops boops Purse seine, Trawl 1 Mar - 15 Dec / 1 Oct - 30 May<br />

Scomber japonicus Purse seine 1 Mar - 15 Dec<br />

Trachurus trachurus<br />

Trachurus mediterraneus<br />

Spicara smaris<br />

Scomber scombrus<br />

Sarda Sarda


Eutrophication/Land-based inputs – Thermaikos gulf<br />

Possible scenarios<br />

different water discharge (Climatic change)<br />

different nutrient loads and N/P from Axios river based on EUROCAT project<br />

(simulated by MONERIS catchment model under different assumptions regarding policies, agriculture<br />

development etc)<br />

• Fertiliser plants<br />

• P-free detergents<br />

• Urban waste<br />

• 1. BAU<br />

Nikolaidis et al., 2009<br />

2. Policy Target<br />

3. Deep green


Eutrophication/Atm-Deposition - <strong>Aegean</strong><br />

Atmospheric deposition plays a significant role in the oligotrophic <strong>Aegean</strong> <strong>Sea</strong> as is one of<br />

the main routes of nutrients into the marine environment<br />

Possible scenarios<br />

different atmospheric deposition (Climatic change of rainfall ±10%)<br />

different nutrient load composition in the deposition<br />

Land-based inputs/Acidification<br />

different Alkalinity input (provided by WP1?)<br />

Organic pollutants (Thermaikos)<br />

Possible scenarios<br />

different loads (Marco?)


Session 3. GES indicators for the N. <strong>Aegean</strong><br />

Descriptor 3: Populations of all commercially exploited fish and shellfish are within<br />

safe biological limits, exhibiting a population age and size distribution<br />

that is indicative of a healthy stock.<br />

Level of pressure of the fishing activity<br />

Descriptor 4: All elements of the marine food webs<br />

Productivity (production per unit biomass) of key species or trophic groups<br />

Abundance /distribution of key trophic groups/species<br />

Descriptor 5: Human induced eutrophication<br />

Nutrient levels<br />

Direct effects of nutrient enrichment<br />

Descriptor 8: Concentration of contaminants are at levels not giving rise to pollution<br />

effects<br />

Effects of contaminants


Session 4. Scenarios<br />

Fisheries<br />

Coupled ERSEM-OSMOSE scenarios:<br />

Equilibrium (no change, constant harvesting of species)<br />

Different changes in effort (Fishing days, No. of boats)<br />

Change in closed fishing areas (geographical or depth related)<br />

Change in closed fishing seasons (Purse seines, trawlers)<br />

Eutrophication/Land-based inputs/Atm-Deposition<br />

Thermaikos riverine inputs - variation in discharge and nutrient load<br />

N. <strong>Aegean</strong> atmospheric inputs - variation in inputs and quality (?)<br />

Pollution<br />

Thermaikos riverine inputs – variation in organic pollutants load

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