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Effects of Wildfires on Runoff and Erosion
Lee H. MacDonald
Watershed Science Program
Colorado State University, Fort Collins, CO
Contributors
• Tedd Huffman (M.S., 2002);
• Juan Benavides-Solorio (Ph.D., 2003);
• Joe Wagenbrenner (M.S., 2003);
• Matt Kunze (M.S., 2003);
• Zamir Libohova (M.S., 2004);
• Jay Pietraszek (M.S., 2006);
• Daniella Rough (M.S., 2007);
• Duncan Eccleston (M.S., 2008);
• Keelin Schaffrath (M.S., 2009);
• Darren Hughes (M.S., 2010);
• Ethan Brown (M.S., 2009);
• Dr. John Stednick;
• Isaac Larsen (Research Assistant, 2004-2007);
• Sergio Alegre (visiting Ph.D. student, 2010).
Why the concern about wildfires?
Hayman Fire, Colorado: August 2004
Channel incision from a 20 mm/hr rain event after
the Cerro Grande Fire near Los Alamos, NM
Photo by John Moody, USGS
Alluvial fan from Saloon Gulch extending into
the South Platte River, Summer 2004(2 years after burning!)
Post-fire Hydrology
Objectives
1. Provide a process-based understanding of the effects of wild and prescribed fires on soils, runoff, and erosion;
2. Evaluate the relative importance of different controlling factors on post-fire erosion rates;
3. Determine the rate of recovery to pre-fire conditions;
4. Discuss how post-fire processes and recovery vary with increasing scale, and put the effects of wildfire in a broader context.
Post-fire Effects Vary with Burn Severity
1) High severity: complete consumption of organic horizon and alteration of the structure or color of the underlying mineral soil; loss of aggregates (“pulverization”):
2) Moderate severity: consumption of litter layer but no visible alteration of the surface of the mineral soil;
3) Low severity: only partial consumption of the surface litter.
Severity is not equal to intensity (heat loss per unit width per unit time), but severity and intensity often assumed to be closely correlated;
Why the sharp increase in runoff and
erosion after some high-severity wildfires?
1. Loss of canopy decreases interception and
evapotranspiration, increasing runoff;
2. Loss of litter decreases interception and exposes soil to
raindrop impacts (increased erodibility) and sealing;
3. Loss of soil organic matter disaggregates or pulverizes
the soil, and this increases soil erodibility;
4. Increase in soil water repellency can decrease
infiltration and increase surface runoff;
5. Loss of litter decreases surface roughness and
increases runoff velocities, increasing erosion;
Effects are synergistic, but which is most important?
Soil Water Repellency
Fire-induced soil water repellency
(DeBano, 1981)
Methods of Analysis
Water drop penetration time (WDPT):
• Apply drops at different depths, beginning at mineral soil surface;
• Indefinite waiting time;
• Assesses persistence of soil water repellency.
Critical surface tension test (CST):
• Apply 5 drops of de-ionized water;
• If 4 of 5 drops are not absorbed within 5 seconds, test
solutions with progressively higher ethanol concentrations
(increasing ethanol concentrations decrease surface tension);
• Critical surface tension (CST) is the tension of the first
solution that is readily absorbed into the soil (“strength”).
Critical surface tension in wild and
prescribed fires: High-severity sites(bottom two sites are prescribed fires)
30
40
50
60
70
80
0 3 6 9 12 15 18
Depth (cm)
Cri
tical su
rface t
en
sio
n
(dyn
es c
m-1)
Crosier M tn.
Hi M eadows
Bobcat
Lower Flowers
Dadd Bennett
Huffman et al., 2001
Critical surface tension in wild and prescribed
fires: Moderate-severity sites(bottom two sites are prescribed fires)
30
40
50
60
70
80
0 3 6 9 12 15 18
Depth (cm)
Cri
tical su
rface t
en
sio
n
(d
yn
es c
m-1)
Hi M eadows
Crosier M tn.
Bobcat
Lower Flowers
Dadd Bennett
Huffman et al., 2001
Critical surface tension in wild and prescribed
fires: Low severity sites(bottom two sites are prescribed fires)
30
40
50
60
70
80
0 3 6 9 12 15 18
Depth (cm)
Cri
tical su
rface t
en
sio
n
(d
yn
es c
m-1) Hi M eadows
Bobcat
Crosier M tn.
Lower Flowers
Dadd Bennett
Huffman et al., 2001
30
35
40
45
50
55
60
65
70
75
0 2.5 5 7.5 10 12.5
Depth (cm)
Me
dia
n c
riti
ca
l su
rfac
e t
en
sio
n (
dy
ne
s c
m-1
)
Unburned
Summer 2002 (10 months)
Summer 2003 (22 months)
Summer 2004 (34 months)
Median soil water repellency over time,
Star Fire, Tahoe National Forest
E. Chase, M.S.. thesis, Colorado State Univ., 2006
Mean soil water repellency by depth:
Unburned vs. burned sites, summer 2002
30
40
50
60
70
80
0 3 6 9 12Depth (cm)
Cri
tica
l su
rface
ten
sion
(d
yn
es c
m-1
)
Hayman fire (n=36)
Schoonover fire (n=18)
Trumbull: unburned
(n=39)
D. Rough, 2007
Soil water repellency from 2002-2004:
Upper Saloon Gulch, Hayman fire
30
35
40
45
50
55
60
65
70
75
80
0 3 6 9 12
Depth (cm)
Cri
tic
al s
urf
ac
e t
en
sio
n (
dy
ne
s c
m-1
)
2004
2003
2002
No water repellency
D. Rough, 2007
0 2 4 6 8 10 12 140
2
4
6
8
10
12
14
0
0.4
1
2
3
4
Meters
Mete
rs
Spatial variability in soil water repellency:
Plot H1, high severity, Hayman fire
Moles of
ethanol
per liter
Woods et al. 2007, Geomorphology
Summary: Soil Water Repellency
• Soils in unburned areas usually water repellent;
• Fire-induced water repellency is usually shallow
(maximum of 9 cm);
• May be stronger in prescribed fires due to higher fuel
loadings and slower rate of fire spread;
• Very high spatial variability;
• Relatively rapid recovery (≤ 2 years);
• Not present under wet conditions (~10-35 percent soil
moisture), depending on fire severity;
• CST faster and more consistent than WDPT.
Supporting Data
Three papers on my web site (type “Lee MacDonald” into google):
1. Huffman, E.L., L.H. MacDonald, and J.D. Stednick, 2001. “Strength and persistence of fire induced soil hydrophobicity under ponderosa and lodgepole pine, Colorado Front Range”, Hydro. Proc. 15: 2877-2892.
2. MacDonald, L.H., and E.L. Huffman, 2004. “Persistence and soil moisture thresholds”, Soil Sci. Soc. Am. J. 68: 1729-1724;
3. Doerr, S.H., R.H. Shakesby, and L.H. MacDonald, 2009. “Soil water repellency: a key factor in post-fire erosion?” In Restoration Strategies after Forest Fires, edited by A. Cerda and P.R. Robichaud, Science Publishers, Inc., Enfield, NH.
Sediment Production at the
Hillslope Scale
Untreated
High severity 319
Moderate severity 55
Low severity 34
Treated (all high severity)
Seeding and scarification with seeding 36
Straw mulch and straw mulch with seeding 60
Contour-felled logs 44
Ground-applied hydromulch 20
Aerially-applied hydromulch 20
Polyacrylamide 12
Total 600
Total plot years of data by treatment
0.0
2.0
4.0
6.0
8.0
10.0
High Moderate Low
Sed
imen
t yie
ld (
Mg
ha
-1)
Fire severity
Summer Rainfall (Jun-Oct)
Snowmelt (Nov-May)
Sediment yields by fire severity and season:
First two years after burning (Colorado)
Role of surface cover,
recovery over time,
and rainfall intensity
Sediment production: Summer 2001 (before Hayman fire)
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1 2 3 4 5 6 7 8 9 10
Pairs of sediment fences (n = 20)
Sed
imen
t (k
g/m
2)
Mean percent ground cover in Upper Saloon Gulch in
2001 (prior to burning) and 2002 (after the Hayman fire)
0
10
2 0
3 0
4 0
5 0
6 0
7 0
8 0
9 0
10 0
1\ 8 1\ 9 1\ 12 1\ 13 1\ 14 1\ 15 1\ 16 1\ 17 1\ 18 1\ 19 1\ 2 0 1\ 2 1 1\ 2 2 1\ 2 3 1\ 2 4 1\ 2 5 1\ 2 6 1\ 2 7 1\ 2 8 1\ 2 9
Swale
Gro
un
d c
over (
%)
2001
2002
Sediment from 11 mm of precipitation in
45 minutes on 21 July 2002
Sediment production after Hayman fire:
21 July 2002 storm (11 mm in 45 minutes)
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
1 2 3 4 5 6 7 8 9 10
Pairs
Sed
imen
t (k
g/m
2)
Control
"Treated" (not
implemented)
Year 2001
69% Bare soil
Year 2002
17% Bare soil
Year 2000, 15 days after fire
96% Bare soil
Vegetation recovery over timeBobcat fire, sediment fence #9
Year 2003
12% Bare soil
y = -26.09Ln(x) + 70.03
R2 = 0.63
y = -21.86Ln(x) + 45.75
R2 = 0.60
y = -10.44Ln(x) + 26.21
R2 = 0.49
0
20
40
60
80
100
0 1 2 3 4 5 6 7 8 9 10
High severity
Moderate severity
Low severity
Time since burning (years)
Pe
rce
nt b
are
so
ilPercent bare soil vs. time since burning
y = 0.0029e0.095x
p < 0.0001
R2 = 0.61
n=345
0
10
20
30
40
50
0 20 40 60 80 100
Sediment yield vs. percent bare soil
Percent bare soil
Sedim
ent yie
ld (
Mg h
a-1
yr-
1)
Event-based sediment production vs. I30:
High-severity wildfires
R2 = 0.62
R2 = 0.50
0
2
4
6
8
10
0 10 20 30 40 50
30-minute maximum intensity (mm hr-1
)
Mean
sed
imen
t p
rod
ucti
on
(M
g h
a-1
)
1-3 years after burning
4-5 years after burning
Sediment production over time:
Pendola fire, Eldorado N.F.
Post-fire erosion vs. percent bare soil:
Pendola fire, Eldorado N.F.
Percent Bare Soil (%)
Sedim
ent p
roductio
n (t h
a-1
yr
-1)
0 10 20 30 40 50 60 70 80 90
0
2
4
6
8
10
12
14
16
181999-20002000-20012001-2002
y=0.12900.0577x
R2=0.77p=0.01
Is all this sediment coming from:
(a) rainsplash and sheetwash on
the hillslopes; or
(b) rill, gully, and channel erosion?
Upper Saloon Gulch: 10 July 2002
17 mm rain in 2 hours
Sediment yields from swales vs.
planar hillslopes in 2001: Bobcat fire
R2 = 0.57
p = 0.01
R2 = 0.53
p = 0.0070
0.2
0.4
0.6
0.8
1
1.2
1.4
0 50 100 150 200 250
Erosivity (MJ mm ha -1 h-1)
Sed
imen
t p
rod
ucti
on
(kg
m-2
)
Planar hillslopes 2001 Swales 2001
Measuring rill erosion, Hayman fire
Rill erosion in Swale 4: Storm on 21 August 2003
-40
-30
-20
-10
0
0 10 20 30 40 50 60 70 80 90 100
cm
cm
15-Aug-02
23-Aug-02
-25
-20
-15
-10
-5
0
0 10 20 30 40 50 60 70 80 90 100
cm
cm
15-Aug-02
23-Aug-02
-40
-35
-30
-25
-20
-15
-10
-5
0
0 10 20 30 40 50 60 70 80 90 100
cm
cm
15-Aug-02
23-Aug-02-40
-35
-30
-25
-20
-15
-10
-5
0
0 10 20 30 40 50 60 70 80 90 100
cm
cm
15-Aug-02
23-Aug-02
12
3 4
8 mm rainfall
I30 = 15.6 mm/hr
27.4 MJ mm/ha yr
Estimated sediment from rill erosion vs.
measured sediment: Hayman wildfire
2500
0
500
1000
1500
2000
3000
0 500 1000 1500 2000 2500 3000
26-Jun-03 14-Jun-03 20-Jul-03
12-Aug-03 6-Sep-03 16-Jun-04
28-Jun-04 28-Jul-04 8-Sep-04
1:1
Measured sediment in fence (kg)
Estim
ate
d s
edim
ent
from
rill
incis
ion (
kg)
Inferred sources of runoff and erosion
• About 80% of the sediment is coming from rilling on
the hillslopes;
• These and other data indicate that the post-fire runoff
is coming from the hillslopes, but most of the post-fire
sediment is coming from incision due to concentrated
flows (rill, gully, and channel erosion);
• See also Moody and Martin, 2001; 2009.
Controls on Post-fire Erosion
• Erosion rates most strongly related to percent bare
soil, which is primarily a function of fire severity and
time since burning;
• For a given percent cover and slope, rainfall intensity
is the dominant control, and erosion increases non-
linearly with rainfall intensity or erosivity;
• Soil water repellency can help reduce infiltration after
burning, but the rapid decay and spatial variability
suggests it is not the dominant control;
• Soil type is generally a third-order control, after cover
and rainfall intensity;
• Rainfall simulations and other work suggest that post-
fire soil sealing is limiting infiltration (SSSAJ, 2009).
Runoff and Water Quality at
Catchment Scale
Saloon Gulch and Brush Creek: A Paired Watershed
Study to Investigate the Effects of Thinning
Stream reaches: Summer 2001
Saloon Gulch Brush Creek
Saloon Gulch flume before Hayman fire
Saloon Gulch flume after first post-fire rainstorm
Saloon Gulch flume cleaned out after
first post-fire rainstorm
Saloon Gulch flume after second
post-fire rainstorm
Lower Brush Creek: Upstream of flume
Since runoff rates decline within 2-4 years after burning,
how long will it take to transport the excess sediment
out of this channel?
Bobcat fire, 8 years later: How long
until this becomes a forest again?
Hayman fire, 7 years later: How long
until this becomes a forest again?
Hayman fire,
seven years later:
How long until
this stops eroding
and degrading
water quality?
Buffalo Creek fire, 2009(13 years after burning)
Hypothetical erosion rates over
time from different sources
Ero
sio
n
Background
Wildfires
Thinning
.01
.1
1
10
Time
Roads
Conclusions: Part 2
• High-severity fires can dramatically increase runoff and erosion rates in headwater areas;
• Large sediment deposits in lower-gradient channels can result in long-term degradation of aquatic habitat;
• For more information, see my web site (type “Lee MacDonald” into google).
Questions?