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THE ROLE OF MACROALGAE IN
CARBON SEQUESTRATION
Dorte Krause-Jensen
Department of Bioscience & Arctic Research Center,
Aarhus University, Denmark
8. NORDIC SEAWEED CONFERENCE
- SEAWEED AND SUSTAINABILITY
Grenå
10-11 October 2018
Photo: Greenland kelp forest by Scott Bennett
Photo: Dorte Krause-Jensen Photo: Núria Marbà
Seagrass meadow
Marine forests
Photo: Peter B. Christensen
Kelp/macroalgal forest
Mangrove Saltmarsh
Photo: Stein Frederiksen
OOceab
Seagrasses & macroalgae
• High biomass, slow
turnover
Similaries to forests on
land in terms of serving as
C-sink
Marine macrophytes as a global C-sink (Smith 1981, Science)
O
S
R
The “Blue Carbon” concept“Out of all the biological carbon (or green carbon) captured in the world, over half (55%)
is captured by marine organisms hence it is called blue carbon”
Seagrass, mangrove and saltmarsh cover <0.5% of the sea surface,
yet represent ~50% of C-burial in marine sediments
Nellemann, C., Corcoran, E., Duarte, C. M., et al. (Eds). 2009. United Nations Environment Programme, GRID-
Arendal, www.grida.no
Ecosystem services of marine forests
Gutierrez et al. 2011
McLeod et al. 2011 Front Ecol Environ
C burial of marine forests much faster than of land forests
… coastal wetlands including mangrove
forests, tidal marshes and seagrass
meadows
Photo Credit: Oceana / Juan Cuetos
And macroalgae ??
Macroalgal forests - the most
extended marine forests
mangroves
salt marshes
Ecosystem
Macroalgae
Seagrasses
Mangroves
Salt marshes
Area (mio km2)
3.4* (1.4-6.8)
0.2-0.6
0.14
0.02-0.4*Krause-Jensen & Duarte 2016, Duarte 2017 Biogeosciences
kelp forests Ste
ne
ck
et a
l. 2
00
2. E
nv.
Con
s.
seagrasses
Macroalgal forests – the globally most productive marine forests
Ecosystem
Macroalgae
Seagrasses
Mangroves
Salt marshes
Local net prim. prod.
(g C m-2 yr-1
91-522
394-449
394-1000
438-1100*Krause-Jensen & Duarte 2016. Nature Geoscience. Duarte 2017 Biogeosciences
Global net prim. prod.
(Pg C yr-1)
1.52* (0.13-2.9)
0.06-1.94
0.05-0.15
0.17-0.42
Fate of macroalgae
Duarte & Cébrian 1996. Limnol. Oceanogr.
Buried in algal bed
0.4%
Grazed
33.6%
Remineralised
37.3%Exported
43.5 %Ocean C
sinks?
Locations where macroalgal carbon
storage has been reported
Krause-Jensen & Duarte 2016
Macroalgae on the deep sea floor
Sargassum, Sargasso Sea, 5310 m depthSchoener & Rowe 1970. Deep-Sea Research
Sargassum in guts of deep sea fauna down to 6475 m Wolf 1962. Galathea Reports
Baker 2017. Deep-
Sea Research part II
Estimated
Sargassum biomass
in the deep
sea:0.07–3.75 g fw
m-2
Kra
use
-Je
nse
n &
Du
art
e 2
01
6 N
atu
re G
eo
scie
nce
Krause-Jensen & Duarte 2016
NPP
1521
1020-1961
Unit: TgC yr–1
Macroalgal C-flow
Krause-Jensen & Duarte 2016
NPP
1521
1020-1961
Unit: TgC yr–1
Macroalgal C-flow
Krause-Jensen & Duarte 2016
Unit: TgC yr–1
NPP
1521
1020-1961
Macroalgae support globally important C
sequestration
Ecosystem
Macroalgae
Seagrasses
Mangroves
Salt marshes
Global C-burial rate
TgC yr-1
173 (61-268)*
48.0-112
22.5-24.9
4.8-87.3Duarte et al. 2013. Nature Climate Change, *Krause-Jensen & Duarte 2016. Nature Geoscience.
**Duarte & Krause-Jensen 2017 Export from seagrass meadows.
Contribution by export to C-sinks outside the vegetated habitat
➢ Double the previous C-burial estimate of marine forests
+
30%**
+?
+?
Many shades of macroalgal Blue Carbon
The evolutionary diversity of macroalgae affect
functions and fate of macroalgal C
Traits increasing the likelihood of C-sequestration:
• Recalcitrance
e.g. kelps export 82% of PP vs average 43%
• Low light requirements -> deep, extended pop.
• Large global production
• Capacity for long-distance transport (boyancy)
Biology Letters. 2018
• Macroalgae in BC strategies remain controversial
• De facto recognized - as C-donors to angiosperm BC habitats
• China & Korea have included macroalgae in BC
• Criteria for including macroalgal C in BC✓ Extensive and actionable
✓ Verified Carbon Standard (VCS): GHG emission reduction/removal
must be ‘real’, ‘measurable’, ‘permanent’, ‘unique’ and ‘additional’.
• Key challenges identified
Review (21 papers on macroalgae in BC context)
- e.g. as buffers against ocean acidification
Erling Svensen
Climate change adaptation potentials
Delille et al. 2000
Macrocystis forest, Southern Ocean
Inside/outside seaweed habitat
High Arctic - Disko Bay (24:0) Jun 16-25, 2014
Frida Lindwall
Slope ~10 ppm d-1
0
50
100
150
200
250
300
350
400
12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00
10
12
14
16
18
20
pC
O2
O2
con
cen
trat
ion
(m
g l-1
)KELP FOREST - 24 H PHOTOPERIOD
pCO2
O2
Slope0.015 units d-1
0
100
200
300
400
500
600
700
800
900
7.95
8
8.05
8.1
8.15
8.2
8.25
8.3
8.35
12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00 12:00
Ligh
t (µ
mo
l ph
ot
m-2
s-1)
pH
Light
pH
Krause-Jensen et al. 2016
Marine forests are under pressure
Ecosystem
Macroalgae
Seagrasses
Mangroves
Salt marshes
Tropical forests
Global loss rate
(% yr-1)
0.018*
0.9
1-3/0.07-1.17
1-2
0.5
Krumhansl et al. 2016 Waycott et al. 2009
Rates of loss and gain
SeagrassKelp forest
Duarte et al. 2013 and refs therein, *Krumhansl et al. 2016
Potentials for Climate Change
Mitigation and Adaptation by Seaweed
Aquaculture
Photo: Prof. Wu
SEAWEED FARMING AND BLUE CARBON
MITIGATION VIA: ADAPTATION TO:Ongoing processes:
Food production with reduced CO2 foot print
C-sequestration via export of “unseen” production
Future potentials:
Bioenergy productionsubstituting fossil fuels
Reduction of methane emission via seaweed feed additive to ruminants
Stimulation of land-based production
via seaweed biochar soil amelioration & seaweed prebiotic health benefits to
livestock
Climate benefit of circular nutrient management
Via avoidance of CO2 emissions for synthetic fertiliser production
Ocean AcidificationHigh daytime pH in seaweed to
the benefit of calcifiers
Increased storminess
and sea level riseShoreline protection via
dissipation of wave energy
Oxygen inputs to coastal
watersAvoiding ocean deoxygenation
with warming
Duarte, Wu, Xiao, Bruhn, Krause-Jensen. 2017
Conclusion & perspectives
• Macroalgal forests are hot spots of productivity
and key coastal habitats
• They support globally important C-sequestration
and their inclusion doubles previous Blue Carbon
C-sequestration estimates
• Macroalgal forests also have potentials in climate
change adaptation – e.g. by increasing pH
• Sustainable management of macroalgal habitats
support ecological quality and offers opportunities
to mitigate and adapt to climate change