measurements and models of primary productivity

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Cullen C-MORE 2014 1 Provided by the SeaWiFS Project, NASA/Goddard Space Flight Center and ORBIMAGE Measurements and Models of Primary Productivity Supported by NSERC including OTN 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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Cullen C-MORE 2014

1Provided by the SeaWiFS Project, NASA/Goddard Space Flight Center and ORBIMAGE

Measurements and Models of Primary Productivity

Supported by NSERC including OTN

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”

John Cullen: C-MORE 2013

Source of some reading

2

http://www.ceotr.ca/publications/

for reading lists, [email protected]

MacIntyre and Cullen 2005

Parkhill et al. 2001

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What is marine primary productivity?

Net Primary Productivity (Production)!!

Net rate of synthesis of organic material from inorganic compounds such as CO2 and water!

!Chemosynthesis: chemical reducing power comes from reduced inorganic compounds such as H2S and NH3!!Photosynthesis: reducing power comes from light energy!!Photosynthetic primary production is usually measured and considered to dominate. !!

g C m-3 h-1 !! !g C m -2 d-1!

Cullen C-MORE 2014

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More to it than that, of course

Doney, S. C.,et al. (2004), Frontiers in Ecology and the Environment, 2(9), 457-466.

John Cullen: C-MORE 2013

Biological oceanography and phytoplankton ecologyDescribe the causes and consequences of variations in

primary productivity (and food web structure)

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Ecological prediction!

Biogeochemical models!

Climate change scenarios

Why measure and model primary productivity?

Behrenfeld et al. Nature 2006

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Oxygenic Photosynthesis

This process can be quantified directly by measuring the increase of oxygen, the decrease of CO2, or the increase of organic carbon. Incubations can be conducted with 14C, 13C or H218O added as tracers.!!The process has many chemical consequences that can be traced with measurements of the concentrations of oxygen and carbon, and their isotopic signatures !!

Cullen C-MORE 2014Annual Review of Marine Science 2013

There are measurements and there are measurements…

Cullen C-MORE 2014

in vitro vs in situ

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In situ estimates need calibration

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Cullen, J.J., 2001. Plankton: Primary production methods. In J. Steele, S. Thorpe, K. Turekian (Eds.), Encyclopedia of Ocean Sciences (pp. 2277-2284): Academic Press.

Biological Oceanography (4): John Cullen

Effects of Light on PhotosynthesisNet Photosynthesis = Gross Photosynthesis - Respiration

Respiration is measured directly only in the dark. The light-dependent component is much harder to measure (18O-tracer can be used for that). 12

Biological Oceanography (4): John Cullen

Effects of Light on PhotosynthesisNet Photosynthesis = Gross Photosynthesis - Respiration

Net photosynthesis is negative when irradiance is below the compensation irradiance.13

Biological Oceanography (4): John Cullen

Relating oxygen evolution to carbon assimilation with the photosynthetic quotient

Note that more photosynthesis is required for growth on nitrate because the nitrate must be reduced.

1.0 NO3- + 5.7CO2 + 5.4H 2O! → ! (C5.7H9.8O2.3N) + 8.5 O2 +1.0 OH-

P.Q. = 1.49 (O2 evolved /CO2 consumed)

1.0 NH4+ + 5.7CO2 + 3.4H2O ! → ! (C5.7H9.8O2.3N) + 6.25 O2 +1.0 H+

P.Q. = 1.10

Generalized reactions for growth on nitrate and ammonium

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Cullen C-MORE 2014

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Inevitable comparisons with satellite-based estimates (models)

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What is behind this?

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Still a benchmark: The 14C method for measuring primary productivity

HOT website

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0 1 2 3 4 5D

epth

(m)

Productivity (mgC m-3 d-1)

± s.e.

The 14C method for measuring primary productivity

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An incredibly useful tool for time series and process studies

HOT website

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Ideally, the 14C method measures net primary productivity

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Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

12 - 24 h incubations

Sometimes, it does

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The measurement is subject toartifacts and biases

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0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

12 - 24 h incubations

Hypothesis: uncertainties inherent in the 14C method are being forgotten with important consequences for the estimation of primary productivity using other methods.

Cullen, J.J., 2001. Plankton: Primary production methods. In J. Steele, S. Thorpe, K. Turekian (Eds.), Encyclopedia of Ocean Sciences (pp. 2277-2284): Academic Press.

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The measurement is subject toartifacts and biases

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40

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0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

12 - 24 h incubations

Overestimation due to exclusion of UV-B

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The measurement is subject toartifacts and biases

0

10

20

30

40

50

0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

12 - 24 h incubations

Underestimation due to static incubation at excessive irradiance

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The measurement is subject toartifacts and biases

0

10

20

30

40

50

0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

12 - 24 h incubations

Underestimation due to dilution of intracellular DIC with respired cellular C

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The measurement is subject toartifacts and biases

0

10

20

30

40

50

0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

12 - 24 h incubations

Overestimation due to unnatural accumulation of biomass (disruption or exclusion of grazers)

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The measurement is subject toartifacts and biases

0

10

20

30

40

50

0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

12 - 24 h incubations

Underestimation due to food-web cycling!(microbial respiration and excretion)

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The measurement is subject toartifacts and biases

0

10

20

30

40

50

0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

12 - 24 h incubations

Overestimation due to inadequate time for respiration to be measured

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…and that’s not all:

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)

Productivity (mgC m-3 d-1)

12 - 24 h incubations

Toxicity!

Relief of iron limitation!

Exposure to bright light!

Disruption of fragile cells!for Simulated in situ:!

Poor match of irradiance!

Inappropriate temperature!

Possible diel bias

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Productivity normalized to Chl is biased by:

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0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

12 - 24 h incubations

Changes in Chl during incubations!

Inadequate extraction of Chl by 90% acetone!

Interference from Chl b(fluorometric acid-ratio method)

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and in general…

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Dep

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Productivity (mgC m-3 d-1)

12 - 24 h incubations

Irradiance is not controlled!

Respiration is not accurately measured

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The measurement has its limitations

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Dep

th (m

)Productivity (mgC m-3 d-1)

± s.e.

Net production?

!Gross production?

!Overestimate?

!Underestimate?

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A less skeptical view

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But we use it routinely

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0 1 2 3 4 5

Dep

th (m

)

Productivity (mgC m-3 d-1)

± s.e.

Water column integral is something like !net primary production!(photosynthesis less losses to respiration)

(extent depends on temperature, light and maybe nutrients)

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Regardless, it has served us very well

Time Series

Karl et al. in Williams et al. 2002

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Process studies

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Solving mysteries

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10 15 20 25 30

Equatorial Pacific – 140°W, 0° ± 2° – PBopt

Measurements vs Behrenfeld et al. Models"Mystery Solved"

PB opt (g

C gC

hl-1

h-1

)

Temperature (°C)

VGPM Exponential Model

Revised according to insightsfrom Behrenfeld et al. Nature 2006

Real measurementsfrom JGOFS EqPac

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Direct Measurements will Never Provide Synoptic Estimates of

Productivity

marine.rutgers.edu/opp/

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Continuous measures of optics reveal rates

see

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Ocean chemistry tells the tale — even in the most oligotrophic waters

3 years of O2 at POT: Ken Johnson

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Models are required for many applications

Productivity from ocean color!

Ecological prediction!

Biogeochemical models!

Climate change scenarios

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Photosynthesis normalized to chlorophyll is the foundation of productivity modeling

Pmaxchl ⋅ (1− exp −(α chl ⋅E)

Pmaxchl

$%&

'())

Pchl vs. E relationship! "##### $#####

Behrenfeld and Falkowski L&O 1997

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One approach: model the measurements

Behrenfeld and Falkowski 1997a L&O

! Opt

ical

Dep

th

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Simplified functions describe major patterns

Behrenfeld and Falkowski 1997a L&O

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Is the measured/modeled pattern real?

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Dep

th (m

)

PB (mg C mg Chl-1 d-1)

Measured near-surface inhibition

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Is the measured/modeled pattern real?

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80

100

0 10 20 30 40

Dep

th (m

)

PB (mg C mg Chl-1 d-1)

or an artifact of fixed-depth incubation?

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Measurements must be made on a shorter time scale

Photosynthetron: Controlled laboratory incubation (Lewis and Smith 1983)

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A comprehensive approach

Approach introduced by Jitts, H. R., A. Morel, and Y. Saijo. 1976. The relation of oceanic primary production to available photosynthetic irradiance. Aust. J. Mar. Freshwater Res. 27: 441-454.

Cullen, J. J., M. R. Lewis, C. O. Davis, and R. T. Barber. 1992. Photosynthetic characteristics and estimated growth rates indicate grazing is the proximate control of primary production in the equatorial Pacific. Journal of Geophysical Research 97: 639-654.

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Dep

th (m

)

Chlorophyll a (mg m-3)

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40

50

0 0.4 0.8

Dep

th (m

)

Short-term measurements can detect near surface inhibition

0630 h: Chlorophyll and Pmax are nearly uniform in the 50-m mixed layer

MORNING

PBm . Chl (mg C m-3 h-1)

Principles described by Marra, Harris, Yentsch -- all prior to 1980

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Dep

th (m

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Chlorophyll a (mg m-3)

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0 0.4 0.8

Dep

th (m

)

PBm . Chl (mg C m-3 h-1)

1215 h: Chlorophyll and Potential Productivity are still nearly uniform in the 50-m mixed layer

Is measured near-surface inhibition real?

Assessment with short-term P vs E

MIDDAY

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0 0.08 0.2

Dep

th (m

)

Chlorophyll a (mg m-3)

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0 0.4 0.8

Dep

th (m

)

Surface incubation led to artifact

1530 h: Fixed-depth incubations at the surface are “fried” — an artifact of sustained exposure 35% underestimation of ML productivity

INCUBATED

PBm . Chl (mg C m-3 h-1)

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Conventional 14C: Near-surface inhibition is overestimated

Error at the surface: big

Error for integral: 8%

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80

100

0 10 20 30 40

Dep

th (m

)

PB (mg C mg Chl-1 d-1)

Artifact

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Parameterization of an Artifact?

Consequences for a model: minor except for irradiance dependence of ΣP at higher daily irradiance

Behrenfeld and Falkowski Consumer’s Guide: L&O 1997

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Many models calculate P from measured relationships

From! ! PB vs E!

and ! E vs depth!

and ! ! Chl!

to! daily water column net primary productivity

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80

100

0 0.2 0.4 0.6 0.8 1

P (mg C m-3 d-1)

Dept

h (m

)

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Results can be generalized

0

0.2

0.4

0.6

0.8

1

0 0.2 0.4 0.6 0.8 1

PB / PBopt

Z /

Z 1%(P

AR)

PZ =PoptB ⋅BKPAR

⋅ f (EPAR (0)Ek)

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Maximum PB is still a key parameter for most models

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20

40

60

80

100

0 2 4 6 8 10PB (g C g Chl-1 h-1)

Z (m

)

Even the spectral ones — even the quantum-yield models

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Compared to other measures, PBopt is

relatively insensitive to artifact

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20

40

60

80

100

0 10 20 30 40D

epth

(m)

PB (mg C mg Chl-1 d-1)

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Global assessment of primary productivity requires global assessment of maximum PB

Behrenfeld and Falkowski 1997b L&O

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PBopt modelled as a function of

temperature

Behrenfeld and Falkowski 1997b L&O

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Two commonly used functions

Behrenfeld and Falkowski 1997b L&O

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8

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Max

imum

PB (g

C g

Chl-1

h-1

)

Temperature (°C)

B & F VGPM

Eppley - type(e.g., Antoine et al 1996)

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You may have seen the figure

Behrenfeld and Falkowski 1997b L&O

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Here are the measurements

Rutgers OPP Study Data Base

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30

35

40

0 5 10 15 20 25 30

Max

imum

PB (g

C g

Chl-1

h-1

)

Temperature (°C)

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Compared with more measurements

Texas Shelf

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40

0 5 10 15 20 25 30

Max

imum

PB (g

C g

Chl-1

h-1

)

Temperature (•C)

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and more measurements!

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40

0 5 10 15 20 25 30

Eppley Type ModelVGPMRutgers OPP DataTexas Shelf & SlopeHOTBATSEqPacArabian Sea JGOFSRoss Sea JGOFSAntarctic PFZ JGOFSPBmax Texas (SL)

Max

imum

PB (g

C g

Chl-1

h-1

)

Temperature (•C)

The foundations of VGPM

Behrenfeld and Falkowski 1997 L&O Underlying data + a few more data sets

Published Statistical Fit Measurements (note scale)

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General functions of T cannot capture major causes of variability in water column productivity

± 2x error

-3

-2

-1

0

1

2

3

-5 0 5 10 15 20 25 30 35

ln(m

easu

red/

mod

eled

)

Temperature (°C)

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Conclusion: General functions of T cannot capture major causes of variability in water column productivity

Relative Error

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We must appreciate the implicationsof this unexplained variability

Carbon cancels out!

…and implications of a carbon-based model that isn’t

!Times Cited: 353 (from Google Scholar, May 2014)

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How much confidence should we have?

Juranek and Quay 2013 Ann Rev Mar Sci

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Estimates like these (NPP) do not yet account for variable physiology beyond central tendencies

Behrenfeld et al. Nature 2006

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The need to compare models with measurements

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Validation is important

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Model

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Headline

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Published model result

Measurements!show the !

opposite trend

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Time Frame

& Statistics

Matter

Measurements

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Measurements !

(no headlines)

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It is also useful to remember the distinction between models and observations

Follows et al. ModelVGPM model

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Many models cannot be directly verified

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100

1200.4 0.5 0.6 0.7 0.8 0.9 1.0

Mix

ing

Dep

th (m

)

PT / PTpot

20, 40, 60min

Nomixing

8 h4 h

2 h

b

No one is immune!

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Conclusions• Models of primary productivity are a fundamental

requirement for describing and explaining ecosystem dynamics and biogeochemical cycling in the sea

• The models are based on measurements: – The measurements are not perfect – The models are not perfect

• Capabilities and limitations of models should always be considered when they are applied

• Effects of underlying assumptions • Comparison with real measurements when available

• Know your model!