1. Assessing GHG exchange at landscape
scale
Bart Kruijt, Ronald Hutjes, Cor Jacobs, Merit van den Berg,
Christain Fritz, Torsten Sachs, Andrei Serafimovich, Stefan
Weideveld, Wilma Jans
Wageningen University&Research; Radboud University
Nijmegen; GeoForschungs Centrum Potsdam
5. Measuring at landscape scale
Effects of management
GHG exchange of the landscape mosaic
Today:
- Peatland emission measures and monitoring
- Simpler flux measurement on small fields
- Integral landscape and fluxes an inventories: aircraft
fluxes
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6. Drained peatlands
Emission Netherlands: 4.2
million ton CO2
Submerged drains (SMD) a
solution?
Peat
CO2
Peat
Degraded peat
CO2
-60 cm
Ditch
-60 cm
Ditch
Submerged drains
6 m
Winter (wet) Summer (dry)
Business as usual
7. Effect of submerged drains on water
table and Reco
Translucent soil chamber measurements:
Take light response curves to derive
dark flux
PhD research work, Stefan Weideveld
8. Pair of eddy covariance sets on peat
meadows with and without submerged drains
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14. Polar 5 in NE Germany
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Andrej Serafimovich preliminary results
15. 2008 data PH-WUR
Flight Strategy
• Full seasonal cycle, mar08-feb09, weekly flights
• Three routes, representative landscapes
Unique data set
• ~215 flight hours, 40 days, nobs=6102 (after QA)
Stratification
• Temporal m, bm, s
• Soil regions: 5
• 13 LUC types
turbulence probe
Novatel GPS antenna
laser altimeter
infra-red thermometer
net radiation
PAR sensors
LICOR 7500
thermocouple
operator
display
C-Migits
IGPS
antenna
turbulence probe
Novatel GPS antenna
laser altimeter
infra-red thermometer
net radiation
PAR sensors
LICOR 7500
thermocouple
operator
display
C-Migits
IGPS
antenna
16. Footprint of airborne measurements
Ede
is footprint model (Kljun, 2004 BLM)
Method Dis-aggregation (DFMR)
footprint analysis: fractional areas cover class in footprint
of airborne flux observation (right)
find cover class-specific fluxes FK by multiple regression or
other (constrained) linear solvers (left)
p x 1 vector of airborne
flux observations
p x n matrix of coverclass
fractional areas,
footprint weighted
n x 1 vector of errors
n x 1 vector of coverclass-
specific fluxes
17. Extrapolate and map fluxes
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𝑭𝒄 𝒍𝒐𝒄𝒂𝒍
𝑷𝑨𝑹 𝒍𝒐𝒄𝒂𝒍
× PAR 𝒂𝒓𝒆𝒂 = 𝑵𝑬𝑬 𝒂𝒓𝒆𝒂, (DAY!)
(Hutjes & Kruijt in prep)
19. So far: daytime only. How get 24-hour NEE?
Aircraft can only fly in DAYTIME
What is lacking is nighttime/ Ecosystem respiration
● Get it from zero-intercept of NEE light response?
● Need to fit non-linear light response on
sparse data – difficult!
● Response is linear on LONGER time scales
● But is that useful?
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20. Is night-time NEE predictable from day-
time NEE?
Daytime or GPP fluxes are ‘easy’:
- good turbulence for EC
- Aircraft can fly
- Remote sensing works
- Photosynthesis well understood
Is NEEnight / NEEday
predictable?
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21. A ‘quick look’ at
(NEEnight / NEEday)/night hr
Analysed a few EC tower data data sets
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22. A ‘quick look’ at
abs [(NEEnight / NEEday)/night hr]
Analysed a few EC tower data data sets
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(low values)
Vegetated,
MINERAL soil gives
reasonably
consistent ratio.
Peat soil and bare
soil give higher
values
23. Still some work
to do!
- Comparative flux
measurements at small
fields
- Develop satisfactory
routine measurement
methods
- Extend aircraft flux
inventories to include
nighttime/dark flux
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