s. lan smith ocean sciences meeting 2012
TRANSCRIPT
Feb. 23, 2012S. Lan Smith
Optimality-based modeling of plankton for use in Earth-system modeling S. Lan Smith1, Markus Pahlow2,
Agostino Merico3, Kai W. Wirtz4, Andreas Oschlies2
1Japan Agency for Marine-Earth Science & Technology (JAMSTEC), Yokohama2Leibniz Institute of Marine Sciences at Kiel University (IFM-GEOMAR)
3Leibniz Center for Tropical Marine Ecology (ZMT), Bremen4Helmholtz Center for Materials & Coastal Research, Geesthacht
Ocean Sciences Meeting 2012 Salt Lake City
Feb. 23, 2012S. Lan Smith p. 2
Assumptions
Natural Selection produces optimally adapted organisms
Fitness = Growth Rate Goal-oriented
Considerable success over the past decade
Recent Developments: models of optimal foraging & Primary Production
Major Challenge
Dynamic models consistent with Evolutionarily Stable Strategy (ESS) ESS formulated in terms of steady state (John Maynard Smith)
i.e., how to describe short-term dynamics, e.g., acclimation, consistent with evolutionary adaptation of the very ability to acclimate.
from the review by Smith et al. (Limnology & Oceanography 56, 2011)
Optimality-based models of plankton
Feb. 23, 2012S. Lan Smith p. 3
Acclimation vs. Adaptation
Acclimation short-term changes e.g., seasonal change of a dog’s coat of hair
Adaptation long-term changes evolution (genetic changes in a species) species succession (changes in community composition)
The same approaches can be used to model both. e.g., Wirtz and Eckhardt (Ecol. Mod., 1996), Merico et al. (Ecol. Mod., 2009)
Feb. 23, 2012S. Lan Smith p. 4
Optimality at different levels of organization
Nutrient uptake, e.g., Optimal Uptake
as in Smith et al. (2009)
N used for other enzymes
(max. rate)
N used for uptake
sites(affinity)
nutrient uptake
Autotrophic growth, e.g., iron-light-nitrogen
colimitation as in Armstrong (1999)
phytoplankton
iron used for light
harvesting
iron used for N
assimilation
N uptakelight
phytoplankton
nutrients zooplankton
defenseuptake
Community dynamics, e.g., grazers and phytoplankton
as in Merico et al. (2009)
Maximal net growth rate
Maximal specific growth rate
Maximal uptake rate
Quantity being
optimized
trade-off
(Smith et al. L&O 2011, fig. 2)
Feb. 23, 2012S. Lan Smith p. 5
Trade-offs as ‘Hyper-Parameterizations’
‘Hyper-Parameters’ in hierarchical Bayesian modeling specify prior distributions of model parameters (e.g.,Gelmanetal.Bayesian Data Analysis,2ndedition,2004)
Trade-offs specify how the shapes of functional relationships may change, rather than fixing their shapes. Optimal Uptake kinetics
log NO3 (in seawater)
log K N
O3
-2.5 -1.0 0.0
-3
-2
-1
0
n = 61 data pts.
0 200 400 600 800 1000
0.0
0.2
0.4
0.6
0.8
1.0
0 200 400 600 800 1000 0 200 400 600 800 1000
Upt
ake
Rat
e
NO3 in incubation expts.
Adaptive Response
Smith et al. (MEPS 2009)
V max
KNO3
Trade-off
Feb. 23, 2012S. Lan Smith p. 6
Shape-shifting of the Growth vs. Irradiance curve
RubiscoCHLa CarotPigments
Q Q0
?
f R
DIN
loss
f θ
1-f θ-f R
lossCO2
C-uptake
N-uptake
PONPOC
Gro
wth
Rat
e
Max
. Gro
wth
Rat
e
Light
Flexible Response
Wirtz & Pahlow (MEPS 2010)
Optimal Resource Allocation subject to Trade-offs
Feb. 23, 2012S. Lan Smith p. 7
New interpretations from optimality-based modeling
1. Instead of ‘Inhibition of NO3 uptake by NH4‘ -> co-limitation by Fe, light and nitrogen (Armstrong L&O 1999)
2. Instead of either multiplicative models or Liebig’s Law of the min. -> co-limitation by N, P and light (Pahlow & Oschlies MEPS 2009)
3. Instead of fixed Droop-type quota equation -> saturating response from optimization (Wirtz & Pahlow MEPS 2010)
4. Instead of Q10 ~ 2 for phytoplankton -> Q10 ~ 3 for N uptake inferred from field obs. (Smith JGR 2011)
These have implications for ecology & Earth-System Modeling.
Feb. 23, 2012S. Lan Smith p. 8
T sensitivity for phytoplankton
CO2
Inorganic C Organic C
sinking & exportNo Net Effect on Uptake or Export
CO2
Inorganic C Organic C
sinking & exportwarming
CO2
Inorganic C Organic C
sinking & exportLess Uptake & Less Export
CO2
Inorganic C Organic C
sinking & exportwarming
Standard Assumption: Degradation has greater T sensitivity than Production
However, if Production has the same T sensitivity as Degradation
Common view: Bacteria are more T sensitivity than Phytoplankton. Q10 ~ 2 to 3 (Pomeroy and Wiebe. Aquat. Microb. Ecol. 2001)
OU kinetics applied to field obs. implies: Q10 ~ 3 for nutrient uptake (Smith. GRL 2010, JGR 2011), rather than Q10 ~ 2 (Eppley. 1972).
Feb. 23, 2012S. Lan Smith p. 9
Differences between species: Large-scale patterns of dominanceLitchman et al. (Ecology Letters 10, 2007) “Thesetrade-offs,arisingfromfundamentalrelationssuchascellularscaling lawsandenzymekinetics,definecontrastingecologicalstrategies...[which]can explainthedistributionpatternsofmajorfunctionalgroupsandsizeclasses alongnutrientavailabilitygradients.”
Applications in 3-D models (Follows et al. Science, 2007) & the MIT group.
Monteiroetal.(GBC,2011)‘environmentselects’forN2fixers But how to model more
detailed (finely resolved) & realistic biodiversity?& account for the adaptive capacity of each species?
Feb. 23, 2012S. Lan Smith p. 10
Trait x should change in proportion to its effect on fitness, F:
dx = dx∂F(x,E)
dt ∂x dx: flexibility ~ diversity (trait distribution) E: Environment (light, temperature, etc.)
For plankton F = Growth; dx/dt depends on E (Smithetal.L&O,2011)
Acclimation Rates depend on: 1. possible range of trait values (adaptive capacity), 2. environmental variability 3. current distribution of trait values
Remaining Challenge: modelled diversity tends to collapse immigration required to maintain diversity (Bruggeman & Kooijman L&O 2007)
‘Adaptive Dynamics’: evolutionary changes McGill and Brown (An. Rev. Ecol. Evol. Syst. 2007), Litchman et al. (PNAS 2009) ‘adaptive dynamics’: species succession, communities Wirtz & Eckhardt (Ecol. Modell. 1996), Wirtz (J. Biotech. 2002), Abrams (J. Evol. Biol. 2005)
‘adaptive dynamics’: modelling how fast traits change
Also allows modeling the dist. of x, without discretely resoving it.
Feb. 23, 2012S. Lan Smith p. 11
Different Postulates about the Nature of Life
1. Life is tough and flexible because organisms and species had to be so in order to survive throughout billions of years of evolution (for bacteria & plankton). Pro: Basis for more general understanding New interpretations of obs.
Con: Risk: may over-estimate the ‘Adaptive Capacity of Life’, which does have limits; i.e., may miss some real threats. Humans have driven some species extinct.
2. Life is fragile and inflexible so that any change in environmental conditions might cause Scary Disasters! despite the fact that life evolved experiencing changes in climate & geography. Pro: May identify real threats & risks. Many opportunities for sensational papers (e.g., in Nature), which advance scientists’ careers. Con: Risk: loss of credibility, if predicted Disasters do not occur. No basis for understanding or modeling ‘Adaptive Capacity of Life’.
vs.
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Conclusions
Life is tough and flexible, to a non-neglible extent.
Earth-System Models should account for ‘Adaptive Capacity of Life’.
Optimality-based models are one means to do this using trade-offs as ‘Hyper-Parameterizations’ to constrain adaptive responses.
We need observations to keep this realistic.