Mechanical fuels reduction treatments effects on fire behavior, fuel loads, and forest ecology Osceola National Forest Sept. 28 th, 2011 Sponsors: Conserved.

Slides:



Advertisements
Similar presentations
Diversity of Surface Active Invertebrate Communities at the DePauw Nature Park and Arboretum Aaron Randolph, Department of Biology, DePauw University,
Advertisements

Nitrogen Mineralization Across an Atmospheric Nitrogen Deposition Gradient in Southern California Deserts Leela E. Rao 1, David R. Parker 1, Andrzej Bytnerowicz.
Management of cheatgrass fuel loading in the shrub-steppe Steven O. Link, PhD (Botany) Native Plant Landscaping and Restoration LLC 4604 E. Robin Ct. West.
Introduction to Wildland Fire Behavior
Community and landscape ecology of forest interiors at Merry Lea Aradhana J. Roberts and Jonathon Schramm Goshen College Abstract Introduction Materials.
A brief overview of the Selway Falls Cabin Prescribed Fire This powerpoint is provided to give context to the expected fire behavior and outcomes to the.
Toward Incorporating Climate Change Adaptation into DoD INRMPs in southern California Climate Informed Management & Monitoring Carolyn Enquist, DOI Southwest.
Introduction Methods Results and Conclusions References Acknowledgements Figures and Tables Table 1. Habitat suitability index for forests with different.
Bottomland Forest Ecosystem. Description Bottomland Forests are deciduous, or mixed deciduous /evergreen forests They form closed-canopy forests on riverine.
Overstory and understory vegetation management to meet fire resilience and wildlife habitat objectives Eric Knapp, Becky Estes, and Carl Skinner U.S. Forest.
Fuel Management Objectives within Dry Forest Landscapes on the Okanogan-Wenatchee NF Dr. Richy J. Harrod Okanogan-Wenatchee National Forest.
Comparison of AVIRIS and Landsat ETM+ detection capabilities for burn severity Jan W. Van Wagtendonk, Ralph R. Root and Carl H. Key Presenter Alpana Khairom.
1 Overview of UAA-ENRI’s Studies of the Spruce Bark Beetle Epidemic, Kenai Peninsula, Alaska by Vernon J. LaBau, Univ. of AK., ENRI.
Wendy Gandy Resource Specialist Texas Forest Service.
 Constant warmth and rainfall provides the home to most of the species on Earth.  > 70% of all terrestrial species  Question:  How does the structure.
Delleker North Hazardous Fuel Reduction Fuels & Fire Behavior Assessment Project Funded by the Plumas NF with USDA Forest Service’s “Community Protection”
FIELD METHODS Strategy for Monitoring Post-fire Rehabilitation Treatments Troy Wirth and David Pyke USGS – Biological Resources Division Forest and Rangeland.
One Size Does Not Fit All BUT … Inventory Needs, Purposes and Applications of the National Forests FIA User Group Meeting March 7, 2012 Baltimore, MD.
Relating Post-Treatment Vegetation Responses to Habitat Requirements of Gunnison Sage-grouse Dr. Joe Brummer Colorado State University Department of Soil.
Fire regimes and the World’s biomes 23 September 2010.
Duncan Lutes Systems for Environmental Management Bob Keane – USFS – Research Ecologist, P.I. Carl Key – USGS – Geographer John Caratti – SEM – Systems.
Thesis  Erin Harrington  Advisors  Bobbi Low  Phil Myers.
F.O.F.E.M. 5 First Order Fire Effects Module Adapted from: Missoula Fire Sciences Laboratory Systems for Environmental Management.
o What were we looking at? o The Pit Crew studied soil patterns throughout the landscape.
“Near term response of surface soil nitrogen cycling and pools to forest clearing and burning” Heather E. Erickson Recent soils research from the Teakettle.
Disturbance regimes in restoration ecology: novel effects and ecological complexity Sarah Marcinko November 11, 2005.
Introduction Subalpine meadows play a crucial role in species diversity, supporting many endangered species of plant and wildlife. Subalpine meadows play.
Climate Change and its impact on Forests in Europe and North America Andrew J. R. Gillespie, Ph. D. United States Environmental Protection Agency.
Oct-03FOFEM 5 Overview An Overview of FOFEM 5 Missoula Fire Sciences Laboratory Systems for Environmental Management.
Restoration of Compartment 46 to promote oak-hickory regeneration, shortleaf pine and native grasses in Sewanee, TN Johnson Jeffers and colleagues in FORS.
Wildfire Suppression In Fire Dependent Forests By Jessica Tancordo.
FireBGCv2: A research simulation platform for exploring fire, vegetation, and climate dynamics Robert Keane Missoula Fire Sciences Laboratory Rocky Mountain.
Introduction Oithona similis is the most abundant copepod in the Gulf of Alaska, and is a dominant in many ecosystems from the poles to the sub-tropics.
Introduction to the FIA Down Woody Materials Indicator 1st of 3 Part Training Series Christopher Woodall DWM National Indicator Advisor.
Gradient Modeling Spatial layers of environmental gradients (predictor variables) known to govern rust propagation were compared to percent rust infection.
Natural Disturbance and Environmental Assessments in the Oil Sands Region Linda Halsey April 2012.
AG-WL-3. Why do hunters establish food plots or use game feeders?
Effect of retained trees on growth and structure of young Scots pine stands Juha Ruuska, Sauli Valkonen and Jouni Siipilehto Finnish Forest Research Institute,
Coarse Woody Debris Missouri Ozark Forest Ecosystem Project Missouri Ozark Forest Ecosystem Project Randy G. Jensen Stephen R. Shifley Brian L. Brookshire.
Fire in Florida. Themes l The Natural Role of Fire in Florida l Two Kinds of Fire in Florida l Prescribed Fire l Protecting Florida Homes from Fire.
Aspen stands: Fuel or Fuelbreak at a Landscape Scale?
Silvics Analytic Timing of Site Preparation and Post-Plant Weed Control to Optimize Pine Growth Integration of research results from three region-wide.
Sharon Stanton & FIA National Indicator Leads RECOMMENDATIONS FOR ENHANCED FOREST INDICATORS.
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.
Diel and Seasonal Elk Habitat Selection and Use in the Jemez Mountains Roberts, Caleb; Cox, Robert; Cain, James; Wallace, Mark (1)Elk habitat selection.
U.S. Department of the Interior U.S. Geological Survey Normalized Difference Vegetation Index for Restoration Monitoring Bruce K. Wylie 1, Steve Boyte.
Fuel reduction and defensible space activities among private landowners Jeff Kline Christine Olsen Eric White Paige Fischer Alan Ager.
Effects of simulated climate change on the abundance of an exotic weevil, Cyrtepistomus castaneus Bryan Marbert (ASU ) and Paul Hanson (ORNL) Contact Information:
George Peacock, Team Leader Grazing Lands Technology Development Team Central National Technology Support Center 2010 Southern Regional Cooperative Soil.
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.
S-244 Field Observer & Fire Effects Monitor Fire Effects Monitoring Lesson 2: Methods for Measuring Fire Effects Photo: Marshel Moy.
REPORTS & SUMMARIES S-244 Field Observer & Fire Effects Monitor.
4FRI Biophysical Monitoring Indicators: Assigning Metrics of Success (or Failure) 4FRI Landscape Strategy & Science and Monitoring Working Groups –
Does fertilization influence herbivory during tropical forest restoration? Emma Rosenfield (‘16), Arianna Porter (‘15), Julia Rogers (‘16), Omari Matthew.
Ecological succession How communities and ecosystems change.
June 2016What problems/opportunities/needs are there with forest management? Development of the purpose of and need for action. July 2016What tools are.
Management of cheatgrass fuel loading in the shrub-steppe
Unit 6: Prescribed Burning
School of Forest Resources and Conservation
Unit 6: Prescribed Burning
Ecological succession
Do Now: Fire as an Ecological Disturbance
Fire in Juniper Invaded Sagebrush Steppe
Species Diversity Comparison North and South Slopes
A Comparison of Riparian Vegetation Structures
Vegetation Dynamics of the NE and NW slopes of Betasso Preserve
Ecological Restoration of Standing Dead Wood: Evaluation of the use of bark beetle pheromones and other snag-creation methods to provide standing dead.
L.O: SWBAT explain RADIATIVE BALANCE; how the amount of insolation an area receives, gives off affects its climate and explain DURATION OF INSOLATION (length.
State Climate Office Drought Update
Developing fire regimes and modeling fire restoration for abating the altered fire regime threat at scale Scott Simon, The Nature Conservancy of Arkansas.
Presentation transcript:

Mechanical fuels reduction treatments effects on fire behavior, fuel loads, and forest ecology Osceola National Forest Sept. 28 th, 2011 Sponsors: Conserved Forest Ecosystems Outreach and Research (CFEOR); Southern Fire Exchange (SFE: Joint Fire Science Program; US Forest Service; University of Florida Fire Science Lab Hosts: Jesse Kreye, and David Godwin, PhD Candidates James Camp and Dawn McKinstry, Research Assistants Leda Kobziar, Asst. Professor of Fire Science School of Forest Resources and Conservation, University of Florida Contact us: (352)

Table of Contents Map of treatment locations………………………………….1 Treatment effects on shrubs & litter……………………..2 Understory composition………………………………… Rank of variables among treatments…………………….4 Photo guide……………………………………………………..…5-8 Fire behavior and effects………………………………….9-11 Soil characteristics……………….……………………… Synopses………………………………………………………….….14 Ocean Pond Rd / CR-250A Gum Swamp Rd / CR-250 US HWY-90 Driving Directions Head right (east) on US Hwy-90 approx. 2 miles Turn left (north) on Ocean Pond Rd / CR-250A at the Ocean Pond Campground sign Cross the RR tracks and continue on Ocean Pond Rd over I-10 for approx. 7 miles Turn left (south) on Gum Swamp Rd / CR-250 at stop sign Continue approx. 1 mile experimental units on left Park on the right (north) side of Gum Swamp Rd

Map of Treatment Locations p. 1 Walking Path through Site: Image from ~2 weeks post burn

Osceola NF Fuels Treatment Effects 6 months post-burn & 1 year post-mowing Compartment 69: As of Sept. 25, 2011 p. 2

Osceola NF Fuels Treatment Effects 6 months post-burn & 1 year post-mowing p. 3 Percent Cover of Understory, Litter, and Bare Ground < 0.5 m height

Osceola NF Fuels Treatment Effects 6 months post-burn & 1 year post-mowing p. 4 BiomassControlMowBurnMow + Burn Shrubs1234 Litter1143 Duff1243 Understory Palmetto Cover1324 Palmetto Height1223 Other Shrub Cover2143 Other Shrub Height1243 Percent Cover Shrub (<0.5 m ht.)1432 Grass4132 Herb0100 Ranking 1=highest value 4=lowest value 0=actual value is zero *Underline indicates a relatively larger difference from other values Rank of Values Among Treatments (1 = highest value, 4 = lowest value)

Osceola NF Fuels Treatment Effects Photo Guide- CONTROL p. 5 Treatment: Control Photo Date: May 2011 Location: Osceola National Forest Columbia County, Florida , Fuel Loading

Osceola NF Fuels Treatment Effects Photo Guide- BURN TREATMENT p. 6 Fuel Loading Treatment: Burn Only Treatment Date: February 2011 Photo Date: March 2011 Location: Osceola National Forest Columbia County, Florida ,

Osceola NF Fuels Treatment Effects Photo Guide- MOW TREATMENT p. 7 Fuel Loading Treatment: Mow Only Treatment Date: August 2010 Photo Date: October 2010 Location: Osceola National Forest Columbia County, Florida ,

Osceola NF Fuels Treatment Effects Photo Guide- MOW + BURN TREATMENT p. 8 Fuel Loading Treatment: Mow & Burn Date: Mow: August 2010 Burn: February 2011 Photo Date: March 2011 Location: Osceola National Forest Columbia County, Florida ,

Fuels Treatment Effects on Fire Behavior *Immediate Post-Treatment Conditions p. 9 Potential Fire Behavior – Immediate Post Treatment ( Behave: customized FM9 for post-burned, Hough-Albini for others; actual Rx fire conditions ) X observed (Burned Control) X observed (Mow) X observed (Burned Control)

Fuels Treatment Effects on Fire Behavior *6 months post-burn & 12 mo. post-mowing p. 10 Potential Fire Behavior – Present Day (Behave H-A model; 90 th % wildfire conditions )

Actual Fire Effects on Trees Burn Only and Mow + Burn (burned Feb. 26, 2011) p. 11

Fuels Treatment Effects on Soil T & MC% p. 12 Soil Temperature Burning increased soil T throughout the study period. Mowing reduced soil T in the winter months and increased soil T during the growing season. Soil Moisture Soil MC% was increased in the mowed plots, but less so in the droughty summer season. Increases are likely due to decreased evapotranspiration (ET) and interception, & increased litter cover. Burning initially increased soil MC% in the Burn Only units. Burning in the mowed plots did not have a clear treatment effect relative to the Mow units.

Fuels Treatment Effects on Soil Carbon p. 13 Soil Carbon Soil carbon and soil organic matter did not differ among treatments Soil carbon respiration (SCR) increased from January through July with a decline in August. This trend follows seasonal variations in soil T rather than soil moisture content. Burning in unmowed plots reduced SCR for 2 months. Mowing followed by burning also showed a trend of reducing SCR. Mowing did not show an obvious effect on SCR. Soil Carbon Respiration Rates

Synopses & Take Home Messages p. 14 After 6 mo. Post Burn and 12 mo. Post Mow: Predictions of fire behavior suggest little difference among treatments for rate of spread Predictions suggest greater flame lengths in Control, and slightly greater FL in Mow units. Burn and Mow + Burn have virtually indistinguishable fire behavior, suggesting it is similarly mitigated by both treatment scenarios. Observed Fire Behavior & Effects on Trees: After 6 mo. regrowth, Mow units had lower flame lengths and rates of spread than Burn Only Behave underpredicted actual fire behavior in Burn Only units. Mowing prior to burning effectively reduced percent crown volume scorch and TCD. Bark beetles and tree mortality are present in the Burn Only, but not the Mow + Burn units. Vegetation and Ground Cover: 6 and 12 mo. post treatments, litter cover was near 50% in all treatments Burned units had more bare ground and grass than control units Mow Only units had the highest grass and herbaceous component Palmetto and other shrub height, cover, and biomass were reduced by all treatments. Take-Home Messages 1.Although burning, (either following mowing or alone), mitigates potential fire behavior immediately post treatment, at six months post-burn fuels and vegetation recovered so that potential rate of spread would was no longer affected by treatment. However, flame lengths appear to be greatly reduced by all treatments when compared with controls, even after this recovery time period. 2.Mowing increases percent cover of herbaceous and grassy species, increasing functional diversity and potentially improving wildlife habitat. Mechanical disturbance to soils may be responsible for these effects. 3.Burning during the dormant season after Mowing decreases herbaceous and grass components of the understory, when compared with Mow alone. 4.Mowing long-unburned sites prior to reintroduction of fire reduces fire behavior, decreases crown scorch and tree mortality, and results in low fire risk. We found no evidence of increased bole or fine root damage in Mow + Burn sites. 5.Soil carbon and soil organic matter are not affected in the short-term by treatments; however, burning appears to decrease soil carbon loss and increase soil temperatures. Caveat: Although we have 113 plots across the forest, the data presented herein were generated from the demonstration site in compartment 69 for the purpose of this workshop. Our data collection is continuing, and our ultimate analyses will include data from all of the sampled areas, reflecting trends across the greater landscape. Conclusions may, therefore, change as the additional data are tested.