FireBGCv2: A research simulation platform for exploring fire, vegetation, and climate dynamics Robert Keane Missoula Fire Sciences Laboratory Rocky Mountain.

Slides:



Advertisements
Similar presentations
The Central Washington Landscape Assessment (CWLA) project update and discussion.
Advertisements

Historical Creation of Early Seral Habitat: Fire, Wind, Bugs …
Dry-conifer Ecology and Silviculture in Western Oregon John D. Bailey Oregon State University.
Watershed Wildland Urban Interface Modeling Impacts of Potential Climate Change and Associated Wildfire Occurrences on the Levels of Sustainable Resources.
MODELING THE IMPACTS OF CLIMATE CHANGE – CHANGES MADE IN A SPECIES SPECIFIC MODELING SYSTEM Jim Chew, Kirk Moeller, Kirsten Ironside Invited presentation.
Rapid River Schools FOREST ECOLOGY “Conservation is a state of harmony between men and land.” “A Sand County Almanac” Aldo Leopold
SIMulating Patterns and Processes at Landscape scaLEs HISTORIC RANGE of VARIABILITY.
Silvicultural experiments exploring linkages between stand structural diversity and ecological variables in California Carl Skinner, Martin Ritchie, Eric.
How many possums and where? The National Possum Model James Shepherd & Mandy Barron.
Stand Structure and Ecological Restoration Charles W. Denton Ecological Restoration Institute John D. Bailey, Associate Professor of Forestry, Associate.
Dave Sauchyn, Ph.D., P.Geo. C-CIARN Prairies Prairie Adaptation Research Collaborative Senate Committee on Agriculture and Forestry Ottawa, December, 2002.
Modelling Natural Regeneration in Mountain Pine Beetle Affected Stands A Hybrid Model Approach Derek Sattler, M.Sc. Candidate Faculty of Forestry. University.
Climatic and biophysical controls on conifer species distributions in mountains of Washington State, USA D. McKenzie, D. W. Peterson, D.L. Peterson USDA.
Climate Change as a Driver in Mountain Pine Beetle Outbreaks in Eastern Washington Washington State Climate Change Impacts Assessment Conference Seattle,
Examples. Using FEPF to identify priority treatment areas based on soil erosion potential and critical fish habitat In the Bitterroot Valley, MT.
LANDIS 4.0, A New Generation Computer Simulation Model for Assessing Fuel Management Effects on Fire Risk in Eastern U.S. Forest Landscapes Hong S. He.
F.O.F.E.M. 5 First Order Fire Effects Module Adapted from: Missoula Fire Sciences Laboratory Systems for Environmental Management.
Lodgepole Pine / Ponderosa Pine Ecotone By Tyler Bieneman Lodgepole Pine / Limber Pine Ecotone VS. Winter Ecology – Spring 2005 Mountain Research Station.
Reciprocal Disturbance Interactions in Pinus albicaulis Ecosystems Nancy Bockino – M.S. Candidate Daniel Tinker – Advisor University of Wyoming Department.
LANDIS-II Workshop April 1, LANDIS-II Workshop Agenda 1.Introduction to LANDIS-II presentation 2.Tour of the Web Site 3.Downloading new extensions.
Effects of Climate Change on Pacific Northwest Ecosystems Dave Peterson.
Effects of Climatic Variability and Change on Forest Resources Dave Peterson Forest Service – PNW Research Station Pacific Wildland Fire Sciences Lab UW.
Dendroecology March 31, Dendroecology Dendroecology is the analysis of ecological issues such as fire, insect outbreaks, and stand-age structure.
CLASS UPDATES Office hours: Fridays 9AM-12noon (or me for an appointment) Powerpoints – on class website Schedule changes: thesis statement, outline,
Computer modelling ecosystem processes and change Lesson 8 Presentation 1.
Concerns Related to Whitebark Communities Whitebark Pine Distribution of Whitebark Pine in the GYE W hitebark pine occurs in the upper subalpine zone of.
Blending Science with Traditional Ecological Knowledge  Frank K. Lake  Environmental Science, Graduate Ph.D program  US Forest Service- Redwood Sciences.
Measuring Habitat and Biodiversity Outcomes Sara Vickerman and Frank Casey September 26, 2013 Defenders of Wildlife.
UPPER MONUMENT CREEK LANDSCAPE RESTORATION Allan Hahn – District Ranger Mike Picard – ID Team Leader.
Combining historic growth and climate data to predict growth response to climate change in balsam fir in the Acadian Forest region Elizabeth McGarrigle.
4 Forest Restoration Initiative Overview of Vegetation Data, Modeling and Strategies Used to Develop the Proposed Action Neil McCusker Silviculturist 4FRI.
Spatial Modeling of Whitebark Pine in Three Rocky Mountain Ecosystems FEScUE Program, Summer 2009.
SIMULATING THE IMPACT OF AREA BURNED ON GOALS FOR SUSTAINABLE FOREST MANAGEMENT Jimmie Chew, RMRS Christine Stalling, RMRS Barry Bollenbacher, Region One.
Application Landscape Ecology in Forest Management: A Glass Half Empty? Thomas Spies USDA Forest Service Pacific Northwest Research Station.
. Wildfires Elkford Impacts and Opportunities More Fuel in Forest Drier Forest Increase in suitable range of Mountain Pine Beetle Warmer annual average.
Stefan Zeglen, Forest Pathologist, West Coast Region Jim Brown, Senior Analyst, Forest Analysis and Inventory Branch CSC Winter Workshop, Nanaimo, BCFebruary.
Limits and Possibilities for Sustainable Development in Northern Birch Forests: AO Gautestad, FE Wielgolaski*, B Solberg**, I Mysterud* * Department of.
How do forest ecosystems respond to environmental change?
Gradient Modeling Spatial layers of environmental gradients (predictor variables) known to govern rust propagation were compared to percent rust infection.
Fire-climate-vegetation- topography-land use What drives and determines fire patterns across time and space? What are the implications of global climate.
SPATIALLY EXPLICIT MODELING OF COLORADO PLATEAU LANDSCAPES FROM CONCEPTUAL MODELS TO A COMPUTER SYSTEM Chew, Jimmie D., Kirk Moeller, and Chris Stalling.
Extension of the forest ecosystem simulation model FORECAST: incorporating mountain pine beetle, fire, climate change, and wildlife Hamish Kimmins, Kim.
FORESTRY TEST BASICS. How To Measure the Diameter of a Tree? Stand next to the trunk (if on an non-level slope – then stand on the uphill side of the.
Modeling the effects of forest succession on fire behavior potential in southeastern British Columbia S.W. Taylor, G.J. Baxter and B.C. Hawkes Natural.
An Adaptive Management Model for the Red River Basin of the North.
Fire, birds, bears and trees Conservation and restoration of whitebark pine ecosystems.
What questions are researchers asking in order to understand fire ecology? Landscape perspectiveSpecies perspective How does the ecosystem, topography.
Climate change and wildfire Research at the PNW Station: past, present, future Don McKenzie (TCM/FERA) with contributions from PNW Science Day March 12,
Southern Interior Forest Region Soils Plant Ecology Hydrology Geomorphology Silvicultural Systems Wildlife Ecology Forest Science Program Research, Consultation,
Global Change and Southern California Ecosystems Rebecca Aicher UCI GK-12 March 7, 2009.
Virtual Experiment © Oregon State University Models as a communication tool for HJA scientists Kellie Vache and Jeff McDonnell Dept of Forest Engineering.
Introduction to Models Lecture 8 February 22, 2005.
The role of climate in sugar maple health: Historical relationships and future projections.
What is a prairie?.
USING THE FOREST VEGETATION SIMULATOR TO MODEL STAND DYNAMICS UNDER THE ASSUMPTION OF CHANGING CLIMATE Climate-FVS Version 0.1 Developed by : Nicholas.
Ecological Site Descriptions Foundation for Resource Management Decisions George Peacock Grazing Lands Technology Institute USDA-NRCS.
Multiscale Climatic, Topographic, and Biotic Controls of Tree Invasion in a Sub-Alpine Parkland Landscape, Jefferson Park, Oregon Cascades, USA Harold.
Fire, birds, bears and trees Conservation and restoration of whitebark pine ecosystems.
SIMulating Patterns and Processes at Landscape scaLEs HISTORIC RANGE of VARIABILITY.
Fairy Lake Rx Burn Monitoring Stated objectives:  Mimic light to moderate ground fire  To minimize the mortality of mature whitebark pine (
Restoring whitebark pine ecosystems in the face of climate change pine Bob Keane, USDA Forest Service Rocky Mountain Research Station Fire Sciences Laboratory.
The Effect of Fuel Treatments on the Invasion of Nonnative Plants Kyle E. Merriam 1, Jon E. Keeley 1, and Jan L. Beyers 2. [1] USGS Western Ecological.
Enabling Ecological Forecasting by integrating surface, satellite, and climate data with ecosystem models Ramakrishna Nemani Petr Votava Andy Michaelis.
Biodiversity in Functional Restoration Joan L. Walker Southern Research Station Clemson, SC.
Forest Management Service Center Providing Biometric Services to the National Forest System Program Emphasis: We provide products and technical support.
How is science like sausage?
Historical and physiographical determinants of tree species distribution in human-dominated boreal landscapes Yan Boucher, Pierre Grondin and Isabelle.
Figure 1. Spatial distribution of pinyon-juniper and ponderosa pine forests is shown for the southwestern United States. Red dots indicate location of.
Identifying Adaptation Management Options for Whitebark Pine in the Greater Yellowstone Ecosystem May 22, 2013.
Angela Gee, US Forest Service July 22, 2019
Presentation transcript:

FireBGCv2: A research simulation platform for exploring fire, vegetation, and climate dynamics Robert Keane Missoula Fire Sciences Laboratory Rocky Mountain Research Station USDA Forest Service 1

Natural Resources Canada

Multi-scale controls on fire Field and empirical studies become more difficult  Moritz M. A. et.al. 2005. PNAS;102:17912-17917 Extension of traditional fire triangle concept - Climate/weather and fuels changing over time, multiple scales. Multiple interactions – climate/weather influence plant growth, fire dynamics: vegetation/landscapes are shaped by fire and succession, but also influence burning patterns. Controls on fire at different scales. Dominant factors that influence fire at the scale of a flame, a single wildfire, and a fire regime. This is an extension of the traditional “fire triangle” concept (20, 21), here including broad scales of space and time, the feedbacks that fire has on the controls themselves (small loops), as well as feedbacks between processes at different scales (arrows).

So much to simulate… What model? The best models to explore climate change dynamics integrate complex ecological processes over spatial and temporal scales Complex interactions at fine scales eventually become manifest at coarse scales Models without these interactions have limited application Interactions should be across processes & scales

The FireBGCv2 model Ecosystem process simulation Mechanistic, spatially explicit individual tree succession model Ecosystem process simulation Fire ignition and spread Multi-species / multi-age stand dynamics Operates at multiple spatial and temporal scales Captures climate-fire-vegetation interactions Landscape Site Stand Species Tree FireBGC = Fire BioGeoChemical succession model 500 year simulation period Model complexity Uncertainty – what do we learn? How to use models in management? Five hierarchical levels of organization are implemented into Fire-BGC. The coarsest level is the landscape. Nested under the landscape are static polygons called sites that have similar topography, soils, weather and potential vegetation. Each site is composed of a number of dynamic stands that differ in vegetation composition and structure reflecting past disturbance history. Fire-BGC simulates ecosystem processes on a small portion of the stand called the simulation plot for computational efficiency. Any number of species can inhabit a stand and species composition influences many processes such as canopy dynamics and tree regeneration. The finest level of organization is the tree. Each tree on a simulation plot is explicitly represented in the Fire-BGC architecture and described by a number of attributes including diameter, height and leaf carbon. Trees are not mapped on the simulation plot. Table 1 lists the ecosystem processes simulated at each hierarchical level. Fire-BGC is the fusion of two ecosystem models, each developed from very different approaches. The process-based, gap-replacement model FIRESUM was merged with the mechanistic biogeochemical simulation model FOREST-BGC (Running and Coughlan 1988; Running and Gower 1991) to predict changes in species composition and landscape dynamics in response to changes in various ecosystem processes over long periods. The mechanistic approach of FOREST-BGC improved the level of detail needed to understand those ecosystem processes that govern tree growth and successional dynamics. Fire-BGC simulates the flow of carbon, nitrogen and water across many ecosystem components to calculate individual tree growth and changes in organic biomass on the forest floor. Carbon is fixed by tree needles via photosynthesis using solar radiation, temperature and precipitation as driving variables. The fixed carbon is then distributed to leaves, stems and roots of individual trees, with a portion lost from each tree component each year to accumulate on the forest floor in the litter, duff, and soil. These forest floor compartments lose carbon through decomposition. Nitrogen is cycled through the system from the available nitrogen pool. The carbon allocated to each tree’s stem at year’s end is used to calculate diameter and height growth. Daily weather described by temperature, precipitation, and radiation, influence the flux of carbon, nitrogen, and water to and from each component. The spatially explicit fire simulation model FAIRSITE is linked to Fire-BGC to predict the growth of fire across the landscape once it is started by the FIRESTART model which is also linked to Fire-BGC using the Loki system. FIRESTART stochastically simulates the occurrence or ignition of a fire on the landscape based on Weibull probability distributions stratified by climate and site fire regime. FARSITE uses the spatial data layers of topography, vegetation, weather and fuels to predict fire behavior characteristics such as fireline intensity and rate of spread. Simulation platform

FireBGCv2 is NOT… A prognostic, predictive model Accurate Stable A model that predicts events A model that is used for short-term predictions Accurate Complexity increases uncertainty Stable Highly complex models are inherently unstable

FireBGCv2 is… A regime or cumulative effects model Robust Simulates long-term ecological effects Simulates complex interactions across scales Simulates many disturbances Robust Mechanistic architecture allows wide application A research platform Explore new landscape behaviors Compare various modeling approaches

The Lineage or “Family Tree” of FireBGCv2 H2OTRANS FOREST-BGC BIOME-BGC DAYTRANS FIRE-BGC “Big Leaf” BioGeoChemical Models JABOWA SILVA FIRESUM FireBGCv2 Stand level gap phase models

FIRE-BGC Simulation Design Key Levels of Organization: LANDSCAPE SITE STANDS (Plot) SPECIES TREES

FIRE-BGC Simulation Modeling Processes Simulated at Each Scale Landscape ● Seed dispersal ● Cone crops ● Fire dynamics: Ignition Spread ● Insect and disease occurrence White pine blister rust Mountain pine beetle ● Management action planning ● Climate change ● Hydrology

FIRE-BGC Simulation Modeling Processes Simulated at Each Scale Site ● Weather ● Phenology ● Soils

FIRE-BGC Simulation Modeling Processes Simulated at Each Scale Stand Most important ecological processes are simulated at this scale

FireBGCv2 Stand Components

Stand Level Processes Flow Chart

Fire Effects simulated in FireBGCv2 Stand level

Management Actions Stand Level Various management actions Prescribed burn Timber harvesting (thinningclearcut) Wildland fire use Grazing Wildlife habitat suitability Hydrology Stream temperature

FIRE-BGC Simulation Modeling Processes Simulated at Each Scale Species ● Regeneration ● Phenology ● Fire effects

FIRE-BGC Simulation Modeling Processes Simulated at Each Scale Tree ● Growth ● Mortality ● Regeneration ● Litterfall ● Wildlife habitat ● Snag dynamics

FIRE-BGC Simulation Modeling Dynamic Output ● Tabular and map output available ● Over 890 possible output variables for tabular summaries ● Only 25 map variables ● Output by landscape, site, stand, species, tree

Define resilience and resistance

Modeling tipping points Six temperature factors: 1 °C - 6 °C Seven precipitation factors: 70% - 130% Ecosystem and fire effects How much change is too much? DRIER Define resilience and resistance WARMER

Fire rotation (yrs) Glacier NP Yellowstone NP Bitterroot NF 169 yrs. WARMER DRIER 169 yrs. 223 yrs. 56 yrs.

Tree mortality (%) Glacier NP Yellowstone NP Bitterroot NF 59.7% 70.3% WARMER DRIER 59.7% 70.3% 17.0%

Basal area (m2/ha) Glacier NP Yellowstone NP Bitterroot NF 38.8 m2/ha WARMER DRIER 38.8 m2/ha 26.5 m2/ha 29.6 m2/ha

Basal area thresholds DRIER WARMER 1° 2° 3° 4° 5° 6° 130% 120% 110% Significant (P < 0.5) changes in mean basal area for climate change scenarios for MD-GNP, CP-YNP, and EFBR. Solid fill indicates decreased basal area and hatched fill indicates increased basal area as compared with the no climate change scenario.   1° 2° 3° 4° 5° 6° 130% 120% 110% 100% 90% 80% 70% WARMER DRIER Glacier NP Yellowstone NP Bitterroot NF

Dominant species changes Yellowstone NP Lodgepole pine Douglas-fir

Hypothesized Change Current Climate Climate & Fire Same Forest New Forest Grass Sage Fire Adapted Current Forest Current Climate Climate & Fire Climate does not affect forest Climate creates new forest composition or structure Climate creates vegetation transition Same Forest Same Forest Fire Adapted New Forest New Forest Grassland Same Forest New Forest Grass Sage Fire Adapted Current Forest Current Forest New Forest Fire Adapted New Forest Sage Steppe Present idea of fire and climate as drivers of forest composition and structure. Grassland Grassland Sage Steppe

Climate Basal Area Percent Cover Douglas-fir Non-Forest Lodgepole Pine Same Forest New Forest Grass Sage Fire Adapted Current Forest Basal Area Same Forest New Forest Grass Sage Fire Adapted Current Forest A2 B1 Historic Percent Cover Same Forest A2 B1 Historic New Forest Effect of vegetation, present 100 results Douglas-fir Lodgepole Pine Engelmann Spruce Non-Forest Whitebark Pine Subalpine Fir Photo: US NPS

Climate + Fire Stand Age Percent Cover Douglas-fir Non-Forest Same Forest New Forest Grass Sage Fire Adapted Current Forest Same Forest New Forest Grass Sage Fire Adapted Current Forest Same Forest A2 B1 Historic Stand Age Percent Cover Same Forest A2 B1 Historic Grass Sage Effect of climate on vegetation and fire, present 00 results, also present age distribution box plots. All Fires Historical B1 A2 Fire Rotation 320 y 150 y 120 y Mean Annual Area Burned 483 ha 853 ha 1328 ha Douglas-fir Lodgepole Pine Engelmann Spruce Non-Forest Whitebark Pine Subalpine Fir

Management Percent Cover Douglas-fir Non-Forest Lodgepole Pine Same Forest New Forest Grass Sage Fire Adapted Current Forest Same Forest New Forest Grass Sage Fire Adapted Current Forest Percent Cover 0% Suppression 50% 100% Grass New Forest Fire Adapted Sage 50% Suppress. Historical B1 A2 Fire Rotation 320 y 170 y 302 y Mean Annual Area Burned 483 ha 955 ha 491 ha Suppression on veg, present contrast of 50% or 98 with 00 results, just table. Douglas-fir Lodgepole Pine Engelmann Spruce Non-Forest Whitebark Pine Subalpine Fir Photo: US NPS

FireBGCv2 Limitations Difficult to parameterize Difficult to initialize Long execution times (20-50 hours) Extensive memory requirements (>7 GB) Abundant output Difficult to understand and use Long training time Not really a management model

FireBGCv2 Advantages One of the most comprehensive landscape models available Highly complex, non-linear behaviors Fire-climate-vegetation linkage Runs on any computer Extensive documentation Code available Flexible structure

Final FireBGCv2 Information Coded in C programming language Compiles on any platform Web site: http://www.firelab.org/research-projects/fire-ecology/139-firebgc Implemented for 14 landscapes Used in over 15 projects…