the ecology of iron enhanced ocean productivity michael r. landry integrative oceanography division...
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The Ecology of Iron Enhanced Ocean Productivity
Michael R. LandryIntegrative Oceanography DivisionScripps Institution of OceanographyUniversity of California, San Diego
Funding: National Science Foundation Grants OCE-9908808 and -9911765
Focus: Upper-ocean ecology, not carbon sequestration
Mechanisms & implications
Units of Biomass Response
0
50
100
150
200
250
300
20 30 40 50
PatchControl
Time (year day)
Y = 68,900 * X-1.79
R2 = 0.98
IronEx II SOFeXChl a 16-20 X 20 X
Phyto-C 4-5 X 2 X
SOFeX South PatchPatch Increase
Overstating the caseGrowth interpretations
Phytoplankton Community Response
0
20
40
60
80
< 2 2-5 5-10 10-20 > 20
PROSYNPEUKPRYMPHAEODIATOMDINO
Size Fraction (µm)
CONTROL
< 2 2-5 5-10 10-20 > 200
20
40
60
80
Size Fraction (µm)
PATCH
< 2 2-5 5-10 10-20 > 200
20
40
60
80
Size Fraction (µm)
PATCH
IronEx II
Phytoplankton Community Structure
% Diatoms
Cont PatchIronEx II 4 74
N-SOFeX 5 38
S-SOFeX 66 80
Ph
yto
pla
nkt
on
(m
g C
m-3)
0
20
40
60
80
100
120
140
< 5 5-10 10-20 >20 >100 Total
SouthControlPatch
Size Fraction (µm)
SOFEX - South
flagellates ==> pennates IronEx, N-SOFeXpennates ==> centrics SEEDS+ silicified ==> less silicified EisenEx
Growth and Grazing in IronEx II
Landry et al. (2000)
0
0.5
1
1.5
2
148 150 152 154 156 158 160 162 164 166
µm
Time (Julian Day)
C
2 nM 1 nM 1 nMIron additions
µg
Heterotrophic Protists
0
2
4
6
8
2-5 5-10 10-20 20-40 > 40
HFLAGCHOANOHDINOCILIATE
CONTROL
Size Fraction (µm)
0
2
4
6
8
2-5 5-10 10-20 20-40 > 40Size Fraction (µm)
PATCH
Grazing Regulation
0
20
40
60
80
< 2 2-5 5-10 10-20 > 20
PROSYNPEUKPRYMPHAEODIATOMDINO
Size Fraction (µm)
CONTROL
< 2 2-5 5-10 10-20 > 200
20
40
60
80
Size Fraction (µm)
PATCH
< 2 2-5 5-10 10-20 > 200
20
40
60
80
Size Fraction (µm)
PATCH
IronEx II
µ
g
µ
g
SOFeX Grazers
0
20
40
60
80
< 5 5-10 10-20 > 20 Total
SouthControlPatch
Size Fraction (µm)
SOFeX - South
Bio
mass
(m
gC
m-3)
% PP Grazed: SOFeX IronExInitial 44 38Bloom Peak 90 + 94
Microbial Community Interactions& Sequestration Potential
Strong µ => g enhances nutrient cycling
Diminishes “structural boost” to export ratio
Quality of export -- single cell egesta
Community shifts -- C:Si export ratio, ballast Different suite of diatoms -- high µ, low Si Variable silicification: SOFeX -- 50% Si:C decr
Rollwagen Bollens & Landry (2001)
Growth rate implications:
from Chl ingested/mgC and C:Chl ratio and 20% GGE
Double C biomass d-1
MesozooplanktonIronEx II: Biomass-specific ingestion of phytoplankton increased ~ 20X
MesoZoo Grazing ≈ 10% µ
Explanations ?
H1: Tightly coupled predatory control
H2: Predators find the patch (scale artifact)
H3: Diatom inhibition of egg hatching success
These are examples of ecological issues thatcould be reasonably addressed by larger or longer experiments.
Many are not
Full population and numerical responses, complex life histories
Phenotypic/genotypic selection & adaptations
Cascade and trickle-down effects of larger and longer-lived consumers
Down-stream effects on adjacent ecosystems
Neocalanus in the Subarctic Pacific
Decreasing depth of mid winter Mixed-layer
Monthly-averaged surface density anomaly
Freeland et al. (1998)Whitney et al. (1999) Mackas et al. (1999)
Timing: > 2 month variability in date of maximum biomass, ~1975 trend reversal
Southern Ocean Krill
Recruitment success -- sea ice & diatom blooms
Foraging migrations
Summary
Fe-fertilization experiments have greatly advanced our understanding of open-ocean production ecology. There are clear and recurrent patterns in microbial community response.
Effects on “macro” components of the food web (aka “animals”) are poorly known. Extrapolation to relevant temporal & spatial scales is difficult.
Beyond sequestration, we need to better understand the ecology of HNLC regions in the context of a changing ocean.