THE USE OF ECO-EXERGY IN
OCEANOLOGY:
APPLICATION TO POSIDONIA
OCEANICA MEADOWS
Dorothée Pête, Branko Velimirov & Sylvie
Gobert
Introduction
Exergy = « Useful work a system can perform when
brought into equilibrium with its environment » (Szargut et al., 1988)
= distance from thermodynamic equlibrium
Applying this theory to understand ecosystems and
to detect environmental perturbations
What a mystification!
It’s metaphysics!
Are you crazy?
Thermodynamic theory for Ecosystems
(S. E. Jørgensen)
Thermodynamic
equilibrium = Inorganic soup
Take energy in: Matter Storage in biochemical constituents
Thermodynamic theory for Ecosystems
(S. E. Jørgensen)
Trends to keep away from thermodynamic equilibrium when becoming more complex (Prigogine, 1980)
Loose energy:
Matter Maintenance Trophic webs
Exergy index or eco-exergy: a practical
way to apply the exergy theory to
ecosystems
• Ex (kJ/volume or surface)
= distance between the system and the thermodynamic equilibrium
when the ecosystem is moving away from thermodynamic equilibrium
when the ecosystem is getting closer from its climax, its ecological optimum
= « work capacity possessed by organisms and ecological networks of organisms due to biomass and information embodied in their genome and the amino acid sequence of proteins » (Jørgensen et al., 2010)
i n i i
C
Ex
.
• βi:-β-factor of the ith organism
-defined on a genetic basis: enzymes and proteins, defined by DNA, are driving life processes (Jørgensen et al., 2005)
- kind of approximation of organisms complexity
- higher for « specialised » organisms
- expressed relatively to detritus (no genetic information, only free energy of the organic matter, ≅ 18,7 kJ.g-1)
- ex: β = 1 for detritus, 8,5 for bacteria and 133 for nematods
Exergy index or eco-exergy
Formula:
Specific exergy
(Structural exergy, Silow, 1998) Exsp = expresses the presence of more specialised organisms in the ecosystem
n i i spC
Ex
Ex
Ex = informations on the capacity of the ecosystem
to develop and get more complex
Use of Ex and Ex
spin Oceanology
• 2 main uses:
- Modeling of ecosystems development (plankton dynamics)
Can we use them to detect a
perturbation in a marine ecosystem
early?
Exportation of vegetal biomass Production of vegetal biomass Production of animal biomass Biodiversity hot spotBasis for food webs Spawning and breeding
ground Hydrodynamic protection Stabilizatio n of the bottom Trapping of suspended particules
• Focus ecosystem = Posidonia oceanica meadow - What?
Posidonia oceanica = endemic seagrass of the Mediterranean Sea
• Focus ecosystem = Posidonia oceanica meadow
- Why?
P. oceanica = descriptor of the quality of the Mediterranean
coastal zone
University of Liege:
- Tradition of marine research (Biology, chemistry, physics, modeling)
- Research station in Calvi Bay, Corsica: STARESO (STAtion
de REcherche Sous-marine et Océanographique)
- Years of experience in the Mediterranean Sea with
a special focus on the Posidonia oceanica ecosystem
Can we use them to detect a
perturbation in a marine ecosystem
early?
In Calvi Bay, pristine and perturbated meadows are well known.
Can we use them to detect a
perturbation in an ecosystem early?
Posidonia oceanica meadow has a low turnover.
Sediment = final container of pollutants (sedimentation)
Microbenthic loop: organic matter (OM), microphytobenthos (microscopic algae), meiofauna (microscopic animals), bacteria
Important sub-system in P. oceanica meadows High turnover
Goals
Clarification and validation of the use of Ex and Exsp as
descriptors of anthropogenic perturbations in P. oceanica beds
Effects of nutrients and organic matter inputs which are the main perturbations in the Mediterranean coastal zone
New method to measure and detect perturbations affecting P. oceanica meadows
Sampling
What?
- sediment cores (vertical profile)
- Biomass determination for
every component of the
microbenthic loop.
- sediment and environment parameters
How to validate an index and a method?
• Spatial heterogeneity at small scale
• Comparison between a pristine and a perturbated site • In situ experiments
Sampling sites
10 m, 22 m Small scales Alteration Shading = Reference site Fish farm 22 m Seasonal variations Perturbated site A d a p te d f ro m V e rm e u le n e t a l. , 2 0 1 1 Fr o m S TA R E S O S A From STARESO SASpatial heterogeneity
S T A R E S O 125 cm 25 cm 3 grids
March, June,
November 08,
March 09
12 nodes/grid
(uniform random)
3 cores/node
Results : DIVA analysis
Biomass of bacteria 0-1 cm 1-2 cm 5-10 cm 40 120 50 130 60 140 260 60 140 240 2-5 cmSpatial heterogeneity : Estimation of Ex &
Ex
sp 0 1000 2000 3000 4000 5000 6000 0 1 2 3 4 0-1 cm 1-2 cm 2-5 cm 5-10 cm 0 1000 2000 3000 4000 November 2008 March 2008 June 2008 March 2009 Sediment depth 0-1 cm 1-2 cm 2-5 cm 5-10 cm 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 Sediment depth Median ± range For 10 cm For 1 cm• Important heterogeneity especially for the 1st cm of the
sediment
Most dynamic slice, exchanges with the water column
BUT probably the most affected by environmental perturbations
• The less heterogenous slice is the 5-10 cm
Less dynamic slice and no exchanges with the water column Anoxic conditions for most samples
BUT « old » sediment
Spatial heterogeneity : Ex & Ex
sp 5-10 cm 0 100 200 300 400 0 1 2 3• Important heterogeneity in spite of the choice • No real seasonal variability
Seems stable along the year
STARESO vs. Fish farm:
5-10 cm 0 50 100 150 200 250 300 350 Fish farm STARESO 0.00 0.25 0.50 0.75 1.00 1.25 1.50 1.75 Fish farm STARESO• Awaited results for November 2008 only
Not an estimation…
Median ± range
• No difference in Exsp
No difference in biomass « quality » between sites
• This estimation is not able to catch the difference in EX between sites.
• In November 2008, Ex STARESO>Ex Fish farm
STARESO is closer from the ecosystem climax than the fish farm.
• No difference in Exsp.
No difference in the « complexity » of organisms living in the ecosystem.
The ecosystem is able to adapt itself to this perturbation
In situ experiments: Sediment alteration
Site: STARESO, 10 m depth.
Duration: 3 months (from end of May to end of August 2009). Alteration (mimic pollution by fish farms or dredging):
- 500 ml of sediment were added once a week on 21 marked points in a 3x3 m frame.
In situ experiments: Shading
Shading ( in turbidity because of in nutrients concentration, fish farms, sewages, land farms):
- 3 nets (3x1 m, mesh size: 0,5 mm2) about 50 cm from the
canopy.
- Light extinction: 52 ± 1,6 %
In situ experiment : Ex
5-10 cm 0 50 100 150 200 250 Control 0 50 100 150 200 250 Alteration 0 50 100 150 200 250 Shading• No difference between periods Estimation?
Too short experiment?
In situ experiment : Ex
sp 5-10 cm 0.00 0.25 0.50 0.75 1.00 1.25 1.50 1.75 Control 0.00 0.25 0.50 0.75 1.00 1.25 1.50 1.75 Alteration 0.00 0.25 0.50 0.75 1.00 1.25 1.50 1.75 Shading Median ± range• No real difference between periods
Estimation?
Conclusions
Spatial variability
• Important heterogeneity BUT less important in the 5-10 cm sediment depth zone
Choice of the 5-10 cm sediment horizon to compare samples even if it is maybe less precise
Fish farm vs. STARESO
• Ex STARESO>Ex Fish farm in November 2008 for the 5-10 cm horizon
Ex seems able to dicriminate both sites
In situ experiment
• No difference along the experiment.
• Use of Ex and Exsp as a tool to detect perturbations in the
Mediterranean coastal zone is not easy to validate in this part of P. oceanica ecosystem.
• Important to link the results with environmental parameters to understant why it works or not.
• Work in progress…
Thank you!
Tanks to Loïc Michel, Renzo Biondo, Gilles Lepoint, Sylvie Gobert, Branko Velimirov, people of the STARESO, students, cleaning team, spreading team, repairing team,…