A consistent nutrient to fish model for the Baltic Sea
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1 A consistent nutrient to fish model for the Baltic Sea Wolfgang Fennel Leibniz Institute for Baltic Sea Research (IOW) Warnemünde
2 Real system Different ways to describe the reality Lagrangian follow the path of individuals Eulerian follow the evolution of distributions of inds Limitations many individuals systems require many equations (technical issue) inapplicable to few animal systems Superindividual to repesent very many inds.
3 Lagrangian Real system Eulerian interaction creation and annihilation of inds (birth and mortality) Interaction of superinds of prey and predator interaction of distribution fields through mass flux up- or down the food web. life cycle resolution through mass-class structuring observation, conservation laws properties of superindividual are not directly observable. numbers of inds are not conserved biomass concentration and abundances are directly observable. conservation of mass applies
4 Life cycles and size classes Phytoplankton, cells cycle between two levels of mass mass levels before and after division, (about factor 2) Zooplankton of fish mass vary by several orders of magnitude Biomass B= m N. (m- individual mass, N number of ind.) d dt B m d dt N, phytoplankton d dt B = m d dt N + N d dt m. zooplankton and fish
5 Cohort approach: growth of typical indiviual of mass m and dynamics of number of inds biomass B=Nm N d dt d dt m N = ( g l) m, m( t = m 0 ) = μn, N( t 0 ) = N0. 0 This is equivalent to: where m=b/n d B = μb + ( g l) B, dt d N = μn, dt N( t0) = N0, B( t0) = B0 = N0m Reproduction 0.
6 For many cohorts many equations; at least one for each cohort Biomass approach (no tagging of specific cohorts) characterize stages by mass intervals and count how many inds are in each mass class, fixed number of equations (two for each mass class, no matter how many inds) similar as Eulerian for the derivation, advection terms are needed to promote inds to the next interval if the maximum mass is approached
7 (1) (2) (3) (4) (5) (6) (7) (10) (8) (11) (9) (12)
8 mass sprat Size structured interaction of prey and predator, (food limited; Ivlev function) mass - cod mass herring
9 Predator- prey interaction, (e.g. cod-herring), the predator can eat all smaller prey animals Prey-predator interaction, (e.g. herring cod), the prey can be eaten by all larger predator animals
10 Further dynamic ingredients: Metabolism: respirations- and excretion rates transferring part of the ingested food (or body mass) to nutrients and detritus (rating: good, quantification of parameters can be improved) Reproduction: off-spring approach (rating: reasonable, but needs refinement) Mortality: natural deaths and starvation rates, fishing mortalities, (rating: reasonable, but difficult, partly questionable, needs further consideration) The result is: Warnemuende Food web Model (WFM)
11 Predator (cod): Model-equations WMF (show just a few equations) for biomass and abundance averaged individual mass m=b/n
12 Prey (herring): Model-equations for biomass and abundance Feeding on herring reduces prey biomass and numbers!!!
13 State variables: numbers, biomass, and average growth (weight versus age) Are directly observed in catches and surveys
14 Link to lower food web Two-way coupling (as start use a simple toy model for the NPZD part)
15 Light, T P Z fish Loads N N D D Sed Truncated model l ZD = 0.03 /d Coupled model add action of fish on zooplankton mortality, g Her and g Spra.. A simple periodic physical forcing. Conversion: 1mmolC => 12 mgc => 100 mg = 0.1 g wetmass
16 Coupling the NPZD-model to fish - three channels d N = u( N) P + lpn P + ldn D + lzn Z + dt d P = u( N) P lpn P g( P) Z lpdp, dt d Z = g( P) ZP lzn Z + GF, dt d D = lzn Z + lpn P ldn D ldd D + L sed dt d Dsed = ldd D. sed dt N FD, import + L FN, Feeding of fish on Z Respiration of fish Fish mortality feeds back into D 1mmolC => 12 mgc => 100 mg = 0.1 g wetmass conversion
17 The Baltic Sea Example Cod, eats herring and sprat (zooplanktivors) > 80% of fish biomass
18 Issue what causes interannual variations?
19 Eastern Gotland Basin Jan.-April ( ) phosphate mmol/m³ Eastern Gotland Basin Jan.-April ( ) nitrate mmol/m³ Bottom up? Nutrient loads Top down? Fishing
20 Baseline example: Variation of reproduction conditions (S, O 2 ), fishing on cod, and nutrient input 20
21 cod: numbers per size class/km 3 Scenario S 0 21
22 Simulated catches of herring (H), sprat (S) and cod (C) Scenario S 0 22
23 Scenarios cod fishing reduced after 15 years
24 Scenario S 2 24
25 Scenario S 5 25
26 Scenario S 7 26
27 Scenario S 5 Simulated total catches of herring (H), sprat (S), and cod (C) Scenario S 7 27
28 Fish (num.&mass) and zooplankton (mass) Scenario S 0 Scenario S 7 low predation of Cod decrease in Z Bottom up High predation of Cod increase in Z Top-down 28
29
30 Interactions between upper and lower food web
31 Fluxes between upper and lower parts of the food web S 0 G F zooplankton consumed by fish S 0 L FN fish to nutrient L FD fish to detritus S 5 S 7 Moderation of cod fishing reduces fluxes between upper and lower food web.
32 Budgets of biomass: potential biomass in the NPZD model, fish and total biomass Moderation of cod fishing: NPZD biomass increases fish biomass decreases S 0 S 7
33 accumulated inputs: minus exports: sedimentation ~ fisching ~ N l DD import sed D Her Cod Cod FH B, FC B6 FC B7 6, etc. NPZD
34 the model can describe interannual variations, the key-controls are: Fishing mortality, Reproduction, and External nutrient inputs
35 Opportunity for Theory Skill assessment of truncated models virtually identical results for: N-load: dn/dt ~ mmolc/m³/d, l Z = /d, extra Z mortality, and D-loss - flux into sediments: dd/dt ~ mmolc/m³/d or extra Z-mortality, l Z = /d, and no D-loss Stamp: Exp=30.15; option_mort=1.1; import_n=0.0063g/m³/d (0.003 mmolc/m³/d),
36 Goal for the next years: Transition to a spatially explicit version (full three dimensional) to run fishing and climate scenarios. Issues are, e.g. oxygen, stage resolved zooplankton, migration patterns (success depends also on partnerships in future projects)
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