behavior, physiology and the niche of marine...
TRANSCRIPT
Behavior, physiology and the niche of marine phytoplankton
Ocean Tracking Network
John J. Cullen !
Department of Oceanography, Dalhousie University Halifax, Nova Scotia, Canada B3H 4R2
!2014 C-MORE Summer Training Course
“Microbial Oceanography: Genomes to Biomes”
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A principal goal of microbial oceanography Describing and explaining the
distributions and activities of marine microbes
marine.rutgers.edu/opp/
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…and using this information to describe the causes and consequences of variations in key biogeochemical processes
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Key biogeochemical processes
• Primary production!• Nitrogen fixation!• Denitrification!• Trace gas production!• …and the many other processes that
make those processes possible
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This can be achieved only through an integrated approach
Rothstein et al., Oceanography Mag.
The role of the oceans in Earth systems ecology, and the effects of climate variability on the ocean and its ecosystems, can be understood only by observing, describing, and ultimately predicting the state of the ocean as a physically forced ecological and biogeochemical system.
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Models integrate information
Mick Follows
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So do you
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Physiological Ecology Including Gene Expression
Ocean Observing Systems
Genomics & the other ‘omics
Theory / ModelsProcess Studies
Hydrological & Atmospheric
Optics [+Acoustics]
Physical Chemical
& Biological Oceanography
Assimilative
biogeochemical m
odelsInte
grat
ed in
terd
isci
plin
ary
sens
or s
yste
ms
One Ultimate Target
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Biological oceanography and phytoplankton ecology
marine.rutgers.edu/opp/
Describe the causes and consequences of variations in primary productivity
(and food web structure)
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An overview of established approaches to marine modelling
Prognostic Model
Diagnostic Model
Surface Chl!mg m-2
Fennell et al. 2006
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Approach #1: Observation, analysis, inference (empirical, diagnostic models)
Behrenfeld and Falkowski 1997b L&O
Modeling the pattern in the measurements — not necessarily primary productivity!
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Result: Quantitative predictions that are as good as the data & assumptions that go into them
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Approach #2: Observation, analysis, inference (qualitative, mechanistic, predictive models)
Arrigo, Nature (2005)
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The testing of qualitative, mechanistic, predictive models may be messy
Arrigo, Nature (2005)
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But predictions can be tested with appropriate observations
Arrigo, Nature (2005)Riser and Johnson Nature 2008
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Diagnostic models can be used to test hypotheses rather than to consolidate and interpret observations
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Approach #3: Prognostic models(quantitative, mechanistic, predictive models) -- e.g., BOCGMs
Doney, S. C., M. R. Abbott, J. J. Cullen, D. M. Karl, and L. Rothstein. 2004. From genes to ecosystems: the ocean’s new frontier. Frontiers in Ecology and the Environment 2: 457-466.
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Complexity is added to increase realism and to test hypotheses
Doney, S. C., M. R. Abbott, J. J. Cullen, D. M. Karl, and L. Rothstein. 2004. From genes to ecosystems: the ocean’s new frontier. Frontiers in Ecology and the Environment 2: 457-466.
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Conventionally tested by the “LPG” criterion — but that is changing
Follows, M. J., S. Dutkiewicz, S. Grant, and S. W. Chisholm. 2007. Emergent biogeography of microbial communities in a model ocean. Science 315: 1843-1846.
Looks Pretty Good!
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e.g., Taylor diagrams
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Fundamentally, ecosystem models should predict population dynamics
Daughter Cell
DaughterCell
!Accumulate (Bloom) !Be eaten !Blow up (viral lysis) !Sink !Die (e.g., apoptosis)
Single Cell
Growth Loss
A bit weird, because “population” refers!to species, and many species are often lumped
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Biogeochemical models must include functional groups
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Critical to know the Environmental Influences on the Growth of Phytoplankton: TemperatureLightDaylength Nutrients
Growth vs Temperature
0.00
0.05
0.10
0.15
0.20
0.25
5 10 15 20 25 30
Alexandrium ostenfeldii
Gro
wth
rate
(d-1
)
Temmperature
0.00
0.04
0.08
0.12
0.16
0.20
0.24
0.28
0 500 1000 1500
Growth vs Irradiance
Gro
wth
Rat
e (d
-1)
Irradiance (µmol m- 2 s- 1)
0.00
0.05
0.10
0.15
0.20
0.25
0 2 4 6 8 10 12
Nutrient Uptake Kinetics
Spec
ific U
ptak
e Ra
te (d
-1)
Nitrate Concentration (µM)
0.00
0.04
0.08
0.12
0.16
0.20
0.24
0.28
5 1 0 1 5 2 0 2 5 3 0 3 5 4 0 4 5
Effect of Salinity
Gro
wth
Rat
e (d
-1)
Salinity
Jensen and MoestrupA. ostenfeldii
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Figuring out what to do with exploding knowledge of biological complexity in the ocean
Challenge:
Venter et al. Science 2004
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A big part of the answer is here
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Growth vs Temperature
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Many other things define the growth-niche of marine phytoplankton
From Margalef et al. 1979 in Cullen et al. Oceanography Mag. 2007
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And cell division is only half of the battle!
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Reduction of loss can be as good as an increase
of growth rate
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So rapid growth is not the only strategy for survival / selection
0.0
0.5
1.0
1.5
2.0
2.5
0 2 4 6 8 10 12
Nutrient Uptake
Spec
ific
Rat
e of
Upt
ake
(d-1)
Nutrient Concentration (µM)
I
IIV
max = 2.25 d-1
Ks = 2.0 µM
Vmax
= 1.5 d-1
Ks = 0.5 µM
www.andyslocum.com/images/tortoise&hare.jpg
It’s the gene, stupid!
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Same framework
From Margalef et al. 1979 in Cullen et al. The Sea 2002
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Top-down or bottom-up control?
Sverdrup’s (1955) map of productivity based on vertical
convection, upwelling and turbulent diffusion
Global productivity estimated from remote sensing
(Falkowski et al. 1998)
As presented by John McGowan (Oceanography Mag., 2004)
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Top-down control
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Top-down control
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Global test of the top-down hypothesis?
Myers and Worm Nature 2003Decline of fish stocks since 1960
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Top-down effects?
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Links to useful references
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Many scientific controversies get sorted out in time
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Bottom-up processes
It can be argued that a similarly parsimonious set of factors
determines the distribution of pelagic biomes, each with its
characteristic flora and fauna... Copepods and whales do not
determine which groups of plants will flourish; like the
phytoplankton, they are themselves expressions of the regional
physical oceanographic regime.
(Alan Longhurstʼs section of Cullen et al., 2002, The Sea )
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40
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A Tool for Making Sense of Physically ForcedEcosystem Dynamics:
Margalef’s Mandala
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Not simply temperature, irradiance, nutrients
Cullen et al. 2002, The Sea
LARGER CELLS HIGHER BIOMASS
TRANSIENT & SELF-LIMITING SELECTION FOR RAPID GROWTH
(DIATOMS)
SMALLER CELLS HIGH TURNOVER
COMPETITION FOR NUTRIENTS RETENTION BY RECYCLING
(MICROBIAL LOOP)
LARGER CELLS HIGHER BIOMASS
SLOWER TURNOVER SELECTIVE PRESSURE
TO SEQUESTER NUTRIENTS AND MINIMIZE LOSSES
(e.g., NOXIOUS/TOXIC BLOOMS)Nutrien
ts —
>
LOW BIOMASS SLOW TURNOVER ADAPTATIONS FOR EFFICIENT USE OF LIGHT&NUTRIENTS
(HIGH-LATITUDE “HNLC”)
Turbulence —>
Potential for Production and Export —>
Event-Scale Forcing —> <— Succession
High Turbulence and Low Nutrients
High Turbulence and H
igh NutrientsLo
w T
urbu
lenc
e an
d Lo
w N
utrie
nts
Low Turbulence and High Nutrients
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The challenge: quantitative description of the niches of functional groups
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Critical to know the Environmental Influences on the Growth of Phytoplankton: TemperatureLightDaylength Nutrients
Growth vs Temperature
0.00
0.05
0.10
0.15
0.20
0.25
5 10 15 20 25 30
Alexandrium ostenfeldii
Gro
wth
rate
(d-1
)
Temmperature
0.00
0.04
0.08
0.12
0.16
0.20
0.24
0.28
0 500 1000 1500
Growth vs Irradiance
Gro
wth
Rat
e (d
-1)
Irradiance (µmol m- 2 s- 1)
0.00
0.05
0.10
0.15
0.20
0.25
0 2 4 6 8 10 12
Nutrient Uptake Kinetics
Spec
ific U
ptak
e Ra
te (d
-1)
Nitrate Concentration (µM)
0.00
0.04
0.08
0.12
0.16
0.20
0.24
0.28
5 1 0 1 5 2 0 2 5 3 0 3 5 4 0 4 5
Effect of Salinity
Gro
wth
Rat
e (d
-1)
Salinity
Jensen and MoestrupA. ostenfeldii
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Acclimated growth rate: genotypic
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0.10
0.20
0.30
0.40
0.50
0.60
0 100 200 300 400 500 600
CCMP 1978
Spec
ific
Gro
wth
Rat
e (d
-1)
PAR Irradiance (µmol m-2 s-1)
Species evolve different functions through adaptation and selection
µ(E) = (µmax )(1− e-(E−KC )
(KE −KC ) ) if E > KC
µ(E) = 0 if E ≤ KC
Cullen et al. in prep
Ecosystem modeling ground zero:
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µ as a function of T and E may not be relevant for describing growth rate in
dynamic environmentsStrain CB501
47 µmol m-2 s-1
y = 0.3585x - 2.3346
R2 = 0.9991
0
1
2
3
4
5
6
7
8
9
10
0 20 40
Time (d)
ln(F
l)
Alexandrium fundyense !Growth determined using the method of Brand and Guillard !!Brand, L. E. and Guillard, R. R. L. (1981). A method for the rapid and precise determination of acclimated phytoplankton reproduction rates. J. Plankton Res. 3: 191-201.
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But it is an excellent startfor identifying niches
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Photosynthesis vs Irradiance: phenotypic
0.0
2.0
4.0
6.0
8.0
10.0
12.0
0 500 1000 1500 2000
912410200509PEg
P (g
C g
Chl
-1 h
-1)
Irradiance (µmol m- 2 s- 1)
Species develop different functions through acclimation
0.0
2.0
4.0
6.0
0 500 1000 1500 2000
P (g
C g
Chl
-1 h
-1)
Irradiance (µmol m-2 s-1)
Diatom grown at50 µmol m-2 s-1
Oscillatoria agardhii"metalimnion"
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Photosynthesis vs Irradiance: phenotypic
Strategies to respond to environmental variability are adaptations
0.0
2.0
4.0
6.0
0 500 1000 1500 2000
P (g
C g
Chl
-1 h
-1)
Irradiance (µmol m-2 s-1)
Diatom grown at50 µmol m-2 s-1
Oscillatoria agardhii"metalimnion"
Layer former
Mixer
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Adaptations to oceanic vs coastal conditions
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Oceanic species has much reduced capability for regulation
Rough and ready coastal mixer
Lean but valiant oceanic survivor
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And what about vertical migrators?
Nutrient concentration? !Temperature?
0 2 4 6 8 100
50
100
150
200
Chlorophyll a (mg m -3 )
Dep
th (c
m) Daytime
distribution
Nighttimedistribution
Heat trap
Acrylic cover
PVC column
Water bath
Sampling ends
Thermistor
Light source
Flow
Fluorometer
Pump
Discrete analyses
“Cheap Tank” — A useful tool for studying the
behavior and physiology of phytoplankton
Other mesocosms have been used in a few labs (e.g., M. Estrada)
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Migration studies
Excellent tool for describing behavior in natural gradients of environmental factors !Difficult to specify growth rate in nature !Good for examining interspecific and intraspecific variability in ecologically important traits
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Alexandrium fundyense Results for 6 strains: Growth Rate vs Irradiance
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0 100 200 300 400 500 600
CB 301
D
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0 100 200 300 400 500 600
CB 307
Spec
ific
Gro
wth
Rat
e (d
-1)
Irradiance (µmol m-2 s-1)
E
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0 100 200 300 400 500 600
CCMP 1979
B
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0 100 200 300 400 500 600
CCMP 1980
Spec
ific
Gro
wth
Rat
e (d
-1)
C
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0 100 200 300 400 500 600
CCMP 1978
Spec
ific
Gro
wth
Rat
e (d
-1)
A
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0 100 200 300 400 500 600
CB501
Irradiance (µmol m-2 s-1)
F
John Cullen: C-MORE 2014Top Layer < 5 µM Nitrate RestoredBottom Layer < 5 µM
All hours 301
0.001
0.01
0.1
1
1 0
1 0 0
1000
0 1 0 2 0 3 0
Day
Flu
ore
scen
ce in
Top o
r B
ott
om
Fif
th/
Rem
ain
der
Surface Deep
Behavior showed significant variability:!! Aggregation at top vs bottom all hours
All hours 307
0.001
0.01
0.1
1
10
100
1000
0 10 20 30 40 50
Day
Flu
ore
scen
ce in
To
p o
r B
ott
om
Fif
th/
Rem
ain
der
Surface Deep
All hours 501
0.001
0.01
0.1
1
10
100
1000
0 10 20 30 40 50
Day
Flu
ore
scen
ce in
To
p o
r B
ott
om
Fif
th/
Rem
ain
der
Surface Deep
All hours 1978
0.001
0.01
0.1
1
10
100
1000
0 5 10 15 20
Day
Flu
ore
scen
ce in
To
p o
r B
ott
om
Fif
th/
Rem
ain
der
Surface Deep
All hours 1979
0.001
0.01
0.1
1
10
100
1000
0 5 10 15 20
Day
Flu
ore
scen
ce in
To
p o
r B
ott
om
Fif
th/
Rem
ain
der
Surface Deep
All hours 1980
0.001
0.01
0.1
1
10
100
1000
0 10 20 30
Day
Flu
ore
scen
ce in
To
p o
r B
ott
om
Fif
th/
Rem
ain
der
Surface Deep
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Bouncing around Redfield
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Bouncing around Redfield
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http://www.whoi.edu/oceanus/viewImage.do?id=4950&aid=2387
Azam, F. (1998), Microbial control of oceanic carbon flux: The plot thickens, Science, 280, 694-696.
Chemotaxis!
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Niches abound!
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But what about quantitative prediction?
Rothstein et al. Oceanography Mag. 2006
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Growth must be described as a function of environmental conditions
0.00
0.05
0.10
0.15
0.20
0.25
5 10 15 20 25 30
Alexandrium ostenfeldii
Grow
th ra
te (d
-1)
Temmperature
0.00
0.04
0.08
0.12
0.16
0.20
0.24
0.28
0 500 1000 1500
Growth vs Irradiance
Grow
th R
ate
(d-1)
Irradiance (µmol m- 2 s- 1)
0.00
0.05
0.10
0.15
0.20
0.25
0 2 4 6 8 10 12
Nutrient Uptake Kinetics
Spec
ific U
ptake
Rate
(d-1
)
Nitrate Concentration (µM)
0.00
0.04
0.08
0.12
0.16
0.20
0.24
0.28
5 1 0 1 5 2 0 2 5 3 0 3 5 4 0 4 5
Effect of Salinity
Grow
th Ra
te (d
-1)
Salinity
Jensen and MoestrupA. ostenfeldii
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Functions can be Developed
(Daylength, Irradiance, Temperature, Nutrients)
€
µ = f (D,E,N ,T )
McGillicuddy, Stock, Anderson, and Signell WHOI
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• Requires a huge amount of work with cultures!• Algae should be acclimated to each set of conditions!
– This can require several weeks
• Conditions in nature are almost never so stable!– Phytoplankton are subject to vertical mixing – Vertical migration
• All combinations of Daylength, Irradiance, Nutrients and Temperature are essentially impossible to test
…but
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Summary: µ as a function of environmental conditions
Good for identifying environmental ranges and optima
0.00
0.04
0.08
0.12
0.16
0.20
0.24
0.28
5 1 0 1 5 2 0 2 5 3 0 3 5 4 0 4 5
Effect of Salinity
Gro
wth
Rat
e (d
-1)
Salinity
Jensen and MoestrupA. ostenfeldii
John Cullen: C-MORE 2014
Summary: µ as a function of environmental conditions
Excellent for describing differences between species!!(and variations among strains of the same species)!!Ancient example:!
!Gallagher, J. C. (1982). Physiological variation and electrophoretic banding patterns of genetically different seasonal populations of Skeletonema costatum (Bacillariophyceae). J. Phycol. 18: 148-162. Eppley, R. W. 1972. Temperature and
phytoplankton growth in the sea. Fish. Bull. 70: 1063-1085.
Even more ancient:
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Can we assume that adaptation provides all the raw genetic material for aggregate super-bugs?
see Eppley, R. W. 1972. Temperature and phytoplankton growth in the sea. Fish. Bull. 70: 1063-1085.
Figure from C.B. Miller, “Biological Oceanography” after Smayda, 1976
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A novel approach
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Everything (well, a lot of things) is everywhere and the environment selects
Natural selection in silico
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The microbialassemblage structures the chemical environment
Only some of the ecotypes survive – the number corresponds to environmental complexity
Rothstein et al. 2006
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A test of our understanding of what structures marine ecosystems (LPG)
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Future steps:Assembly and natural selection of microbial communities guided by metagenomics
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A big part of the answer is here
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Future tests: How much biological complexity is needed to describe and predict ecological and biogeochemical variability in the sea?
Dave Karl, Nature 2002
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ConclusionsRelationships between environmental variability and microbial diversity must be described and ultimately predicted to understand the ecology and biogeochemistry of the sea!
Niches abound: wide range of environmental tolerances specialized life-styles (nutrient requirements, alternate modes of photosynthesis ! physiological plasticity vs specialization for stable environments Complexity will never be fully described with numerical models !The degree of model complexity can and should be related to the ecological/biogeochemical question and its scale.
!This can be done — but models must be verified by measurements! Mahalo!