regional ecosystem dynamics and climate feedbacks a. david mcguire ted schuur scott rupp helene...
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Regional Ecosystem Dynamics and Climate Feedbacks
A. David McGuireTed SchuurScott Rupp
Helene GenetEugenie Euskirchen
BNZ Annual Symposium20 February 2015
Regional Ecosystem Dynamics and Climate Feedbacks Questions
(1) How will interactive responses of disturbance regimes, ecosystem structure/function, and successional pathways to future climate variability and change influence regional ecosystem dynamics?
(2) How will projections of regional ecosystem dynamics affect regional energy and water feedbacks to the climate system?
(3) How will projections of regional ecosystem dynamics affect regional CO2 and CH4 feedbacks to the climate system?
Tasks
(1) Couple model of fire regime (ALFRESCO) with model of ecosystem structure and function (DVM-DOS-TEM), incorporate information from empirical studies, and conduct retrospective analysis of the coupled model framework;
(2) Apply the coupled model for future scenarios of climate and analyze changes in ecosystem function/structure at the regional scale;
(3) Analyze water and energy feedbacks among the applications;(4) Conduct factorial experiments for future scenarios of climate
change and evaluate effects of climate and disturbance on estimates of CO2 and CH4
Primary Support for this ResearchIdentifying Indicators of State Change and Predicting
Future Vulnerability of Alaska’s Boreal Forest (funded by DoD SERDP)
Modeling Objective: Develop models that can forecast landscape change in response to projected changes in climate, fire regime, and fire management.
Integrated Ecosystem Model for Alaska and Northwest Canada (funded by USGS and Alaska Landscape Conservation Cooperatives
To develop a conceptual framework for integrating important components of an ecosystem model for Alaska and Northwest Canada including: fire, vegetation dynamics/succession, biogeochemistry permafrost dynamics, and hydrology.
Primary Support for this Research (cont.)Alaska Land Carbon Assessment (funded by USGS)Objectives are to assess: 1) the amount of C stored in ecosystems
of Alaska 2) the capacity of Alaska ecosystems to sequester C, and 3) evaluation of the effects of the driving forces such as climate and wildfire that control ecosystem C balance.
Permafrost Carbon Network (funded by NSF)Address the question “What is the magnitude, timing, and form
of the permafrost carbon release to the atmosphere in a warmer world?” through synthesis by linking biological C cycle research in the permafrost region with well-developed networks in the physical sciences focused on the thermal state of permafrost.
Morning Session (Friday, 20 February 2015): Progress and Future Directions of
Climate Feedbacks Research
8:30 – 8:50 Climate Change and the Permafrost Carbon Feedback – Ted Schuur 8:50 – 9:10 Projections of Climate and Vegetation Change – Scott Rupp 9:10 – 9:30 Consequences for Carbon Feedbacks – Helene Genet 9:30 – 9:50 Consequences for Water/Energy Feedbacks – Eugenie Euskirchen 9:50 – 10:10 Coffee Break10:10 – 10:30 Future Directions for Climate Feedbacks Research – Dave McGuire10:30 – 11:00 Discussion of Future Directions for Climate Feedbacks Research11:00 – 11:15 Overview of Proposal Development – Roger Ruess 11:15 – 12:00 Theme highlights and directions – Other Theme Leaders
12:00 – 1:30 Lunch
Future Directions of BNZ Regional Climate Feedbacks Research
(Dave McGuire Perspective)
(1) Substantial progress on the effects of climate, fire, and top down permafrost thaw in uplands on vegetation dynamics and biogeochemistry. Still work to do (such as insects and pathogens).
(2) Begun modeling research on the effects of thermokarst on wetland vegetation dynamics and biogeochemistry.
(3) Need to begin modeling research on biogeochemical linkages of uplands and wetlands to inland surface waters (lakes and streams) and biogeochemistry of inland surface waters.
Future Directions of BNZ Regional Climate Feedbacks Research
(Dave McGuire Perspective)
(1) Substantial progress on the effects of climate, fire, and top down permafrost thaw in uplands on vegetation dynamics and biogeochemistry. Still work to do.– Finish two-way coupling of ALFRESCO with DVM-
DOS-TEM and GIPL – Additional research on modeling successional
trajectories– Begin research on modeling the dynamics and
effects of insect and pathogen disturbances
ALFRESCO GIPLDVM-DOS-TEM
Burned area
O Horizon Thickness
Vegetation Type Soil Thermal Profile
Vegetation Carbon
Soil Moisture Profile
Moss Thickness
Vegetation Canopy
Elevation, Slope, Aspect. Historical Fire Mineral Soil Texture
Air Temperature, Precipitation, Initial VegetationSnow Water Equivalent
Finish two-way coupling of ALFRESCO with DVM-DOS-TEM and GIPL
Relative dominance of spruce in post-fire recruitment is related to fire severity, pre-fire stand age and drainage conditions.
The drivers of post-fire recruitment composition
Fire severity Drainage Stand age
Johnstone et al. 2010
Drainage
Pre-fire vegetation (PFV)Mesic
SubhygricFailure
High/moderate
lowMixed trajectory
Pre-fire stand ageXeric Pre-fire vegetation (PFV)
< 50 yr
> 50 yrFailure
Mixed trajectory
high
low/moderate
Deciduous trajectory
Pre-fire stand age
Thermokarst ?
< 50 yr
> 50 yrFailure
Evergreen trajectory
PFV = decid.Deciduous trajectory
Fire severityPFV = everg.
PFV = decid.Deciduous
Fire severityPFV = everg.
Thermokarst ?
Regression Tree Approach to Modeling Dynamics of Post-fire Recruitment and Successional Trajectories : Helene Genet
Build Successional Dynamics into DVM – DOS – TEM
(Euskirchen et al. 2009)
The dynamic vegetation model simulates carbon and nitrogen dynamic of various plant functional types, competing for light and nitrogen uptake.
Future Directions of BNZ Regional Climate Feedbacks Research
(Dave McGuire Perspective)
(1) Substantial progress on the effects of climate, fire, and top down permafrost thaw in uplands on vegetation dynamics and biogeochemistry. Still work to do.– Finish two-way coupling of ALFRESCO with DVM-
DOS-TEM and GIPL – Additional research on modeling successional
trajectories– Begin research on modeling the dynamics and
effects of insect and pathogen disturbances
Future Directions of BNZ Regional Climate Feedbacks Research
(Dave McGuire Perspective)
(2) Begun modeling research on the effects of thermokarst on wetland vegetation dynamics and biogeochemistry.– Development of Alaska Thermokarst Model (ATM)– Development of Peatland DOS-TEM/DVM-DOS-TEM– Coupling of ATM with Peatland DVM-DOS-TEM
Quantifying the Area Susceptible to ThermokarstFunction of ice content, landscape position (lowlands), presence of
peat (histels), and presence of permafrost(from Helene Genet)
Conceptual Model of Landscape Change Associated with
Thermokarst Disturbance
PermafrostPlateau
Thermokarst Lake
Young Fen(< ~100 yr old)
Young Bog( < 100 yr old)
FenL
Old Fen Old Bog
Thermokarst-Prone Landscape Change Questions
• What is the current distribution of land cover types in thermokarst-prone landscapes?
• What are the transition rates among land cover types during the satellite era?
• What are the controls over transition rates (e.g., climate, permafrost, hydrology)?
• How is the distribution of land cover types projected to change in the future?
Biogeochemistry Change Questionsin Thermokarst-Prone Landscapes
• How do land cover transitions in thermokarst-prone landscapes (and associated changes in permafrost and hydrology) influence carbon storage and fluxes in land cover types?
• How do land cover transitions (and associated changes in permafrost and hydrology) influence the loading of carbon into lake and stream networks ?
• How will climate change (and associated changes in land cover transitions, permafrost, and hydrology) influence carbon dynamics in lakes, stream networks, and wetland complexes?
Bookkeeping Model: Estimates of Carbon Dynamics of each Land Cover Type
(Jen Harden, Jon O’Donnell, Others)Collapse Bogs (CB)
Delta Shallow SOC (g C m-2 yr-1)
Delta Deep SOC (g C m-2 yr-1)
Delta VEGC (g C m-2 yr-1)
0-50 128 -1085 051-100 108 -488 0
100-500 56 -50 0>500 13 0 0
Permafrost Plateau Forests (PPF) 38 14 0
Treed Bogs (TB) 13 0 0
Net CH4 Emissions(g C m-2 yr-1)
NEE (+ to atmosphere) (g C m-2 yr-1)
DOC Flux(g C m-2 yr-1)
Collapse Fens (CF) 6 -8 2.5
Thermokarst Lakes (TL) 4.6 15 2.5
Bookkeeping Model: Transition Rates(Proportion Per Year)
From/To (Proportion)
Permafrost Plateau Forest
Thermokarst Lake Collapse Fen Collapse Bog Treed Bog
Permafrost Plateau Forest (PPF) NAN 0.0007619 0.0042418 0.0001359 NANThermokarst Lake (TL) NAN NAN 0.0012821 NAN NAN
Collapse Fen (CF) NAN NAN NAN 0.0002 NAN
Collapse Bog (CB) NAN NAN NAN NAN 0.0001
Treed Bog (TB) 0 NAN NAN NAN NAN
Bookkeeping Model: Dynamics of Thermokarst Land Cover Types 1950-2300 Using
Contemporary Transition Rates
Bookkeeping Model: Consequences of Using Contemporary Transition Rates for
Cumulative Changes in Carbon Storage
Raised WT
Lowered WT
Control
Development of Peatland DOS-TEM/DVM-DOS-TEM has relied on data from The Alaska Peatland Experiment (APEX)
A. 1901-2011 B2. 2012-2099 (GFDL) A1B A2 B1
4.5
199 5.7
209 CH4 efflux
HR CO2 efflux
Litterfall C
Soil OC change
SimTP
-2.3
259 5.8
263
Sim0P
9.5
235 6.0
250
SimT0
-5.5
226 4.7
225
Sim00
10.1
234 5.8
250
SimTP
0.6
250 5.8
256
Sim0P
9.4
233 6.0
249
SimT0
-3.0
227 5.1
229
Sim00
9.8
233 5.8
248
SimTP
8.8
251 5.8
266
Sim0P
10.9
242 6.3
259
SimT0
0.7
224 5.3
230
Sim00
11.2
241 6.1
259
from Fan et al. 2013(units are g C m-2 yr-1)
Future Directions of BNZ Regional Climate Feedbacks Research
(Dave McGuire Perspective)
(2) Begun modeling research on the effects of thermokarst on wetland vegetation dynamics and biogeochemistry.– Development of Alaska Thermokarst Model (ATM)– Development of Peatland DOS-TEM/DVM-DOS-TEM
Zhaosheng Fan (now DOE-ANL): FenYanjiao Mi: Collapse Scar Bog, Permafrost Plateau, and
biogeochemical consequences of thermokast disturbance based on data from chronosequence studies.
– Coupling of ATM with Peatland DVM-DOS-TEMThis is an activity of the IEM team (science question: How does coupling (internal feedbacks of the system) influence wetland dynamics and biogeochemistry?)
Future Directions of BNZ Regional Climate Feedbacks Research
(Dave McGuire Perspective)
(3) Need to begin modeling research on biogeochemical linkages of uplands and wetlands to inland surface waters (lakes and streams) and biogeochemistry of inland surface waters.
– Mack et al. DOE proposal in review– TEM6 models DOC and DON loading
Afternoon Session (Friday, 20 February 2015): Quantifying Uncertainty and Understand
Legacies
1:30 – 1:35 Overview of the Afternoon Session – Dave McGuire 1:35 – 1:50 Analyzing Uncertainty in Field/Experimental Research: A
Hierarchical Bayesian Perspective – Colin Tucker 1:50 – 2:05 Role of Model-Data Fusion in Analyzing/Quantifying Uncertainty
– Dave McGuire 2:05 – 2:20 Characterizing Uncertainty in Applications of Ecological Models –
Jeremy Littell 2:20 – 2:40 Perspectives on Studying the Role of Legacies in BNZ Research –
Michelle Mack 2:40 – 3:00 General Discussion
3:00 – 3:15 Coffee Break
Role of Model-Data Fusion in Analyzing/Quantifying Uncertainty
(D. McGuire and H. Genet)
• Sources of Uncertainty in Models• Traditional Parameter Uncertainty Analysis• Model-Data Fusion
Sources of Uncertainty in Modeling
• Conceptual Uncertainty– Compare dynamics of alternative models
• Formulation Uncertainty (equations)– Compare models with different equations
• Parameter Uncertainty– Various approaches to analyzing uncertainty
• Application Uncertainty– Jeremy Littell’s presentation
Traditional Parameter
Uncertainty Analysis• Definition
Relates the variability of model predictions to uncertainty in parameter estimates.
Uncertainty analysis is analyzing the effect of the variance of a parameter to the model predictions.
Multiple parameter uncertainty analyses:100 independent sets of parameters value using Monte Carlo iterations applied to 43 parameters varying within an “acceptable” range, assuming a uniform probability density function for each parameter.
SWHi = Threshold snow water equivalent at which forage intake goes to zero for each ungulate category ; GWP = Water content per kg protein ; FGB = Forage intake per kg of body mass ; BMi = initial body mass for each ungulate category; PSN(24) = Snow depth in unburned forest. From Turner et al. (Ecological Applications).
Model-Data Fusion• Model and data integration, also called model–data fusion or model–data synthesis, is
defined as combining models and observations by varying some properties of the model, to give the optimal combination of both (Raupach et al., 2005). Model–data fusion encompasses both calibration and data assimilation.
• Model–data fusion can be characterized as both an inverse problem, analyzing a system from observations, and as statistical estimation.
• Calibration: Parameter estimation to produce desired outputs for a given input.
• Data Assimilation: observations are used to refine estimates of the evolving model state.
• Model–data fusion brings together four components: – external forcing, – a model that relates model parameters, state and external forcing to observations, – observations, and – an optimization technique.
Example: Uncertainty in the fate of soil organic carbon: A comparison of three conceptually different decomposition models in a larch plantation (He et al. JGR-B in press)
• Compared three structurally different soil carbon (C) decomposition models (one driven by Q10 and two microbial models of different complexity)
• The models were calibrated and validated using four years of measurements of heterotrophic soil CO2 efflux from trenched plots in a Dahurian larch (Larix gmelinii Rupr.) plantation.
• Parameters in each model estimated using a Bayesian data assimilation framework
Differences in Model Dynamics and Uncertainty
Simulated 100 years responses of SOC stock for the three models. Top panel (a-c) is trenched plot simulation; bottom two panels (d-i) are model simulations under 4.8 °C progressive increasing soil temperature and litterfall. The deep blue and red lines (for 3-pool Q10 model) represent ensemble mean from the 100 independent optimization runs for each model, the light colored lines are the results from each ensemble member.
Afternoon Session (Friday, 20 February 2015): How should BNZ quantify uncertainties
and understand legacies?
3:15 – 3:30 Organization of and charge to working groups and discussion points
3:30 – 4:30 Working groups convene 4:30 – 5:30 Working Group Reports 5:30 – 7:00 Mixer, Dinner, Poster Session
Charge to Working Groups
Data and Experimental Uncertainty Group:• How do we quantify uncertainty across the extended
site network?
Model Uncertainty Group:• What aspects of uncertainty should/can be
addressed?• What approaches should be used to addressed
understand/quantify parameter-based uncertainty?• Which data from the extended site network can be
used to address uncertainty?
Legacy Group:
Morning Session (Saturday, 21 February 2015):
BNZ Management and Outreach 8:30 – 9:30 BNZ Site Management – Discussion re gearing up the ESN – Jamie Hollingsworth 9:30 – 9:50 Progress and Directions of BNZ Information Management – Jason Downing 9:50 – 10:15 Progress and Directions of BNZ Education and Outreach – Elena Sparrow 10:15 – 10:30 Coffee Break 10:30 – 10:45 USDA Forest Service Perspective on BNZ LTER – Paul Anderson10:45 – 11:00 LTER Citizen Science – Christa Mulder and Katie Spellman11:00 – 11:15 ITOC – Mary Beth Leigh11:15 – 11:45 Discussion of the Future Directions of BNZ Outreach – Marie Thoms and Alison York 11:45 – 12:00 Organization of and Charge to Afternoon Working Groups – Roger Ruess 12:00 – 1:30 Lunch