Transcript Slide 1
Mechanical fuels reduction treatments effects on fire behavior, fuel loads, and forest ecology Osceola National Forest Sept. 28th, 2011 Sponsors: Conserved Forest Ecosystems Outreach and Research (CFEOR); Southern Fire Exchange (SFE: www.southernfirexchange.org); 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: [email protected]; (352) 846-0901 Table of Contents Map of treatment locations………………………………….1 Treatment effects on shrubs & litter……………………..2 Understory composition………………………………….......3 Rank of variables among treatments…………………….4 Photo guide……………………………………………………..…5-8 Fire behavior and effects………………………………….9-11 Soil characteristics……………….………………………...12-13 Synopses………………………………………………………….….14 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 Ocean Pond Rd / CR-250A • Map of Treatment Locations Walking Path through Site: Image from ~2 weeks post burn p. 1 Osceola NF Fuels Treatment Effects 6 months post-burn & 1 year post-mowing Compartment 69: As of Sept. 25, 2011 p. 2 Percent Cover and Average Height of Shrubs 80 1.4 Avg. Shrub Ht. Palmetto 60 1.2 1 0.8 0.4 Palmetto Palmetto 0.6 Other shrubs 10 Other shrubs 20 Othe r shrubs 30 Other shrubs 40 Palmetto % Cover 50 Height (m) 70 0 0.2 0 Control Mow Burn Mow+burn Litter and Duff Depths and Mass 12 12 Duff mass 10 10 Litter mass Control Mow Burn Duff Depth Litter Depth Duff Depth 0 Litter Depth 2 Duff Depth 4 Litter Depth Mow+burn 4 2 0 Mass (Mg/ha) 6 Duff Depth 6 8 Litter Depth Depth (cm) 8 Osceola NF Fuels Treatment Effects p. 3 6 months post-burn & 1 year post-mowing Percent Cover of Understory, Litter, and Bare Ground < 0.5 m height Burn Control 31 0 42 14 Shrub Shrub 56 Grass Grass Herb Herb Litter Litter 5 Bare Ground 50 0 Bare Ground 0 2 Mow Mow+Burn 24 0 42 4 Shrub Shrub Grass Grass Herb 49 Herb 50 Litter Litter Bare Ground 6 0 24 3 Bare Ground Osceola NF Fuels Treatment Effects 6 months post-burn & 1 year post-mowing p. 4 Rank of Values Among Treatments (1 = highest value, 4 = lowest value) Biomass Control Mow Burn Mow + Burn Shrubs 1 2 3 4 Litter 1 1 4 3 Duff 1 2 4 3 Palmetto Cover 1 3 2 4 Palmetto Height 1 2 2 3 Other Shrub Cover 2 1 4 3 Other Shrub Height 1 2 4 3 Shrub (<0.5 m ht.) 1 4 3 2 Grass 4 1 3 2 Herb 0 1 0 0 Understory Percent Cover Ranking 1=highest value 4=lowest value 0=actual value is zero *Underline indicates a relatively larger difference from other values Osceola NF Fuels Treatment Effects p. 5 Photo Guide- CONTROL Location: Osceola National Forest Columbia County, Florida 30.2657, -82.4919 Treatment: Control Photo Date: May 2011 Fuel Loading Treatment N Control 7 mean sd 1h (Mg·ha-1) 10h (Mg·ha-1) 100h (Mg·ha-1) 1000h S (Mg·ha-1) 1000h R (Mg·ha-1) Litter (Mg·ha-1) Duff (Mg·ha-1) Shrub H-A (Mg·ha-1) Litter Depth (cm) Duff Depth (cm) Palmetto Cover (%) Palmetto Height (m) BA (m2·ha-1) 0.39 0.51 1.60 1.24 0 0 0.25 0.65 0 0 9.49 2.42 14.60 3.39 9.6 8.2 2.1 5.7 1.8 62 24 1.0 0.2 19.4 6.0 Control 30 3.5 Rate of spread 3 Flame length 2.5 20 2 15 1.5 10 1 5 0.5 0 0 0 3 6 9 Windspeed (km/h) 12 Flame Length (m) Rate of Spread (m/min) 25 Osceola NF Fuels Treatment Effects p. 6 Photo Guide- BURN TREATMENT Location: Osceola National Forest Columbia County, Florida 30.2653, -82.4929 Fuel Loading Treatment N Burn 11 1h (Mg·ha-1) 10h (Mg·ha-1) 100h (Mg·ha-1) 1000h S (Mg·ha-1) 1000h R (Mg·ha-1) Litter (Mg·ha-1) Duff (Mg·ha-1) Shrub H-A (Mg·ha-1) Litter Depth (cm) Duff Depth (cm) Palmetto Cover (%) Palmetto Height (m) BA (m2·ha-1) mean sd 0.09 0.11 1.56 1.64 0.27 0.60 4.89 11.82 0 0 2.22 0.62 11.15 2.51 0.30 1.9 0.5 4.0 1.3 18 11 0.5 0.1 18.6 8.3 Burn 3.5 0.7 Rate of spread 3 0.6 Flame length 2.5 0.5 2 0.4 1.5 0.3 1 0.2 0.5 0.1 0 0 0 3 6 9 Windspeed (km/h) 12 Flame Length (m) Rate of Spread (m/min) Treatment: Burn Only Treatment Date: February 2011 Photo Date: March 2011 Osceola NF Fuels Treatment Effects p. 7 Photo Guide- MOW TREATMENT Location: Osceola National Forest Columbia County, Florida 30.2642, -82.4920 Fuel Loading Treatment N Mow 9 1h (Mg·ha-1) 10h (Mg·ha-1) 100h (Mg·ha-1) 1000h S (Mg·ha-1) 1000h R (Mg·ha-1) Litter (Mg·ha-1) Duff (Mg·ha-1) Shrub H-A (Mg·ha-1) Litter Depth (cm) Duff Depth (cm) Palmetto Cover (%) Palmetto Height (m) BA (m2·ha-1) mean sd 0.97 0.45 2.29 1.97 1.16 1.63 0.43 0.84 0 0 12.88 2.40 12.06 2.08 1.2 5.3 1.2 4.4 1.1 11 8 0.7 0.3 20.0 7.3 Mow 25 2.5 Rate of spread 20 2 Flame length 15 1.5 10 1 5 0.5 0 0 0 3 6 9 Windspeed (km/h) 12 Flame Length (m) Rate of Spread (m/min) Treatment: Mow Only Treatment Date: August 2010 Photo Date: October 2010 Osceola NF Fuels Treatment Effects p. 8 Photo Guide- MOW + BURN TREATMENT Location: Osceola National Forest Columbia County, Florida 30.2660, -82.4909 Fuel Loading Treatment N Mow+burn 9 mean sd 1h (Mg·ha-1) 10h (Mg·ha-1) 100h (Mg·ha-1) 1000h S (Mg·ha-1) 1000h R (Mg·ha-1) Litter (Mg·ha-1) Duff (Mg·ha-1) Shrub H-A (Mg·ha-1) Litter Depth (cm) Duff Depth (cm) Palmetto Cover (%) Palmetto Height (m) BA (m2·ha-1) 0.21 0.11 1.35 0.66 0.17 0.50 0.80 1.60 0.06 0.18 1.74 0.58 10.67 3.29 0.0 1.5 0.5 3.7 1.7 4 3 0.3 0.2 22.5 10.3 Mow + Burn 3.5 0.7 Rate of spread 3 0.6 Flame length 2.5 0.5 2 0.4 1.5 0.3 1 0.2 0.5 0.1 0 0 0 3 6 9 Windspeed (km/h) 12 Flame Length (m) Rate of Spread (m/min) Treatment: Mow & Burn Date: Mow: August 2010 Burn: February 2011 Photo Date: March 2011 Fuels Treatment Effects on Fire Behavior p. 9 *Immediate Post-Treatment Conditions Potential Fire Behavior – Immediate Post Treatment (Behave: customized FM9 for post-burned, Hough-Albini for others; actual Rx fire conditions) 30 Predicted Rate of Spread Control 25 Meters/ minute Mow 20 Burn and Mow + Burn 15 X observed (Burned 10 Control) 5 X observed (Mow) 0 0 3 6 (km/h) Wind speed X 3.5 Control 3 12 Predicted Flame Length observed (Burned Control) Mow 2.5 Flame Length (m) 9 Burn MowBurn 2 1.5 1 X observed (Mow) 0.5 0 0 3 6 Wind speed (km/h) 9 12 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; 90th % wildfire conditions) Predicted Rate of Spread 45 Control 40 Mow Meters/ minute 35 Burn 30 MowBurn 25 20 15 10 5 0 0 3 6 Wind speed (km/h) 9 12 Predicted Flame Length 5 Flame Length (m) 4.5 Control 4 Mow 3.5 Burn MowBurn 3 2.5 2 1.5 1 0.5 0 0 3 6 Wind speed (km/h) 9 12 Actual Fire Effects on Trees Burn Only and Mow + Burn (burned Feb. 26, 2011) p. 11 Burn Only: Total Crown Damage (%) Percent Damage (% of crown) 120 y = -3.3125x + 140.2 R² = 0.5983 100 80 60 40 20 0 0.0 20.0 30.0 DBH (cm) 40.0 50.0 Mow + Burn: Total Crown Damage (%) 120 Percent Damage (% of crown) 10.0 100 80 60 40 y = -1.4559x + 79.181 R² = 0.1128 20 0 0.0 5.0 10.0 15.0 20.0 25.0 30.0 35.0 40.0 DBH (cm) No. Trees with % Crown Scorch 12 Burn Only Number of Trees 10 Mow + Burn 8 6 4 2 0 0-10 11-20 21-30 31-40 41-50 51-60 61-70 Percent of Crown Volume Scorched 71-80 81-90 91-100 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 Plots Burned Est. Soil Volumetric Moisture Content (m3/m3) 0.25 Burn Control C D B A 0.20 A B A A Mow BC C AB A Mow+Burn 0.15 B B A A AB B B A 0.10 0.05 0.00 Dec Jan Mar Apr May Jun Jul Aug • 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 Respiration Rates 7.00 Burn Control Soil C02 Respiration Rate μmol CO2 m2 sec-1 6.00 Plots Burned Mow B B A B Mow+Burn 5.00 4.00 C BC A AB 3.00 B A A AB A A B AB 2.00 1.00 DEC JAN MAR APR MAY 2010-2011 JUN Jul Aug 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. 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.