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Data for Monitoring, Reporting, and
Verification: Remote sensing, Inventories, and Intensive sites
Richard Birdsey Carbon Monitoring
Workshop 17 September, 2010
Measurement, Monitoring, and Verification For….
• National Greenhouse Gas Inventories
• REDD and REDD+
• Participation in Carbon Markets (Projects)
• Research and Education
Guías y Requerimientos de Monitoreo
• Existen varias guías, por ejemplo: – IPCC “Guías de Buenas Prácticas” y reportes especiales
– Programas como GEO, GOFC-GOLD, UN-REDD
• Incluir deforestación, degradación forestal y manejo forestal (los métodos pueden ser diferentes)
• Necesidad de flexibilidad para permitir amplia participación, pero los resultados deben ser consistentes
• Necesidad de proyecciones confiables de la línea de base para establecer la adicionalidad
El Enfoque “Multi-tier” de Monitoreo: Observaciones Extensivas con Estudios Intensivos de Procesos del
Ecosistema
• Sensores remotos
• Inventario nacional forestal
• Modelaje
• Sitios de referencia para validación
Selected Land Variables and Measurement Methods
Variable
Remote Sensing
Forest Inventory
Intensive Sites
Land cover X X X
Leaf area X X X
Disturbance X X X
Live biomass X X
Stand structure X X
Species composition X X
Growth, removals, mortality X X
Litter fall X
Soil CO2 flux X
Runoff X
Dissolved Organic C X
Net Ecosystem Exchange of CO2 X
Forest Type Map from Remote Sensing and Inventory
Basic Forest
Inventory Approach
Phase I – Remote sensing to stratify area
Phase 2 – Field inventory
Forest Inventory Phase 3 Sample
• Direct monitoring of additional variables • Not yet included in U.S. greenhouse gas
inventory • Additional variables on subset of P2: soil carbon, down dead wood, forest floor carbon
Condition B = Nonforest Land Use
Condition A =Forest Land Use
Old 1/5-acre plot
US Forest Greenhouse Gas Inventory Data: Currently Based on Phase 2 plots and Ecosystem Models
Carbon estimates are based on tree species and dimensions, forest type, volume of growing stock, and stand age.
Use of Data From Intensive Sites Stand structure and composition Diameter and height
Tree age
Leaf area index
Tree density
Species composition
Carbon pools
Live biomass
Woody debris
Forest floor
Mineral soil
Carbon fluxes
Biomass increment
Litterfall
Forest floor decomposition
Net ecosystem carbon balance
Link to forest classification from inventory (Scaling up)
Data for empirical models based on inventory data
Data for ecosystem process and forest dynamic models
Generalized Biomass Equations by Combining Data from Multiple Studies
0
2000
4000
6000
8000
0 20 40 60 80 100
Ab
ov
eg
rou
nd
bio
ma
ss
(k
g)
aspen/cottonwood
hardmaple/oak
cedar/larch
Douglas-fir
pine
woodland
dbh (cm)
SOURCE: Jenkins and others, 2003
Biomass Related to Volume of Growing Stock: Fitted equation and data points for live trees, Maple-
Beech-Birch, NE region
0
100
200
300
400
0 100 200 300 400
Growing stock volume (m /ha) 3
Bio
mas
s (T
/ha
dry
wt.)
SOURCE: Smith and others, 2003
Forest floor carbon accumulation, decay, and total Example: Southern pines
0
10
20
30
0 25 50 75
Years
Car
bon
mas
s de
nsity
(Mg/
ha)
Mixed or unknown age
SOURCE: Smith and Heath, 2002
accumulation
TOTAL
decomposition
Some Uses of the Data
CO2 Emissions from U.S. Forest Fires Compared with Net CO2 Flux from Forestry and Land-use Change
(From Heath and Smith in US Greenhouse Gas Inventory, 2009)
0
200
400
600
800
1,000
1,200
1,400
1,600
1990 1995 2000 2005
Forest Fire Emissions
Net Forest Sequestration
Million tons CO2 yr-1
-2000
-1000
0
1000
2000
3000
4000
1700 1800 1900 2000 2100
The Carbon Budget of the U.S. Forest Sector
(Forest Ecosystems and Wood Products)
Net Emissions
Net Sequestration
From Birdsey 2006
Year
Mill
ion
to
ns
CO
2 p
er
year
National baseline: -800 MtCO2/yr offsetting 12% of fossil fuel emissions
Basic Information: Total Forest Carbon
Includes all forest ecosystem carbon components, based on FORCARB2 and 2002 RPA Forest Data
Analyze Activities in the Forest Sector to Increase Carbon Sequestration or Reduce Emissions
• Increase forest land area – Avoiding deforestation – Afforestation
• Increase carbon stocks – Mine land reclamation – Forest restoration – Improved forest management – Agroforestry – Urban forestry
• Increase use of wood – Biomass energy plantations – Use wood residues for energy – Substitute wood for other materials
Calculate Emission Factors and Lookup Tables
• Work well when individual reports are summed over a large domains equivalent to that used for derivation of factors
• Tend to smooth over interannual variability over time
• Can be consistently applied at low cost to reporters and verifiers
• May not matter if estimates are consistently wrong (biased) as long as change is accurately estimated
• Reporting and verification burden shifts to documentation of “activity” levels
Sample Output from Landscape Monitoring
• Series of equations: NEP = f(condition, age)
• Hundreds of equations required for diverse conditions
• Example - aggregated estimates for U.S. regions:
-4
-3
-2
-1
0
1
2
3
4
5
6
0-5 5-10 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50
Age Class
t C
per h
a p
er y
ea
r
Southeast
South Central
Northeast
North Central
Rocky Mountain
Pacific Coast
From Pan et al. 2010
Voluntary Reporting Program • Project and entity reporting • Department of Energy, Energy Information
Administration • USDA improving agriculture and forestry
accounting rules and guidelines
Years0 10 20 30 40
Car
bon
(t/ha
)0
50100150200250age 2 carbon
0
50
100
150
200
250
300
0 50 100 150
livec_tphfrom ARG
Pine plantation,
SC
Carbon OnLine Estimator (COLE)
The principal applications of COLE: Greenhouse gas inventories
•Regions, states, groups of counties •User-defined domains •Carbon pools of forest ecosystems
Calculations for greenhouse gas registries
•National registry: 1605(b) •Regional and state registries •Chicago Climate Exchange
COLE is a web-based decision-support tool that queries the U.S. forest inventory database and estimates forest carbon stocks using national standard methodology. Users may select an area of interest as small as several counties, and target specific forest types or conditions.
Source of
Estimate:
Mean NPP
(g C m-2 yr-1)
Std Dev
CASA 491 86
PnET – CN 417 35
Towers 350 75
FIA 250 100
Validation
Teaching and Research Example: Components of NEP Estimation
NEP = (ANPP – RW) + (ΔCFR + ΔCCR + ΔCS – L) Where ANPP = aboveground NPP RW = respiration from woody debris ΔCFR = net change in fine root C ΔCCR = net change in coarse root C ΔCS = net change in mineral soil C L = annual litterfall (From Law et al. 2004)
Potential additional flux terms depending on disturbance and scale (= NBP):
DOC, DIC, VOCs, CH4, particulates,herbivory, tree harvest
Coordination and Consistency for MRV Among Countries With Different Circumstances
!
!
! Hidalgo
Silas Little
Parker tract
Hidalgo
Silas Little
Parker tract
Tropic of Cancer
Summary and Conclusions
• Main products:
– Statistical estimates and maps of carbon stocks and productivity for representative landscapes
– Improved ecosystem models at ecoregion and stand scales
– Decision-support tools for carbon management
– Carbon management research and demonstration sites
• Outcomes of improved forest carbon management:
– Landowners may claim carbon credits
– Cleaner air and lower risk of climate change
• Additional benefit:
– Basis for “early warning” system to detect initial impacts of climate change