joe ditomaso uc davis - sdmmp · 2016. 8. 26. · trigra vicvil brohor vulmyu petnan latcic gerdis...
TRANSCRIPT
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Use of prescribed burning for the control of invasive plants
Joe DiTomasoUC Davis
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Fire is a natural part of many ecosystems
Adenostoma fasciculatum (chamise)
Artemisia tridentata (sagebrush)
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Native California grasslands and oak woodlands were burned nearly every year intentionally by the native peoples
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Three ways fire and invasive plants interact
• Burning can lead to the establishment of new invasive species– Mainly with windblown seed (e.g., Asteraceae)
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Cirsium arvenseCanada thistle
Cirsium vulgarebull thistle
Hypochaeris glabrasmooth catsear
Epilobium brachycarpumTall annual willowherb
Asclepias speciosashowy milkweed
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Three ways fire and invasive plants interact
• Burning can lead to the establishment of new invasive species– Mainly with windblown seed (e.g., Asteraceae)
• Invasive plants can change plant communities by altering the historic fire regimes– Suppression (not common in the western US)– Promotion (very common in the western US)
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Bromus tectorum (downy brome or cheatgrass)
– Historically community composed of bunchgrasses interspersed with long‐lived perennial shrubs
– Historic fire regimes were infrequent (>50 yrs)
– With invasion, fine fuel accumulation was greater than shrub/perennial grass communities
– Dry fuels extended fire season by one to three months
– End result, cheatgrass fires became common, occurring at <5 yrs intervals
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Impacts on vegetation change
– Cheatgrass filled an unoccupied resource niche following fire
– Most native perennials unable to re‐establish in cheatgrass dominated sites
– Native perennial shrubs only revegetatethrough seeds after fire
– End effect is native vegetation replaced with pure patches of cheatgrass
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Impacts on livestock, wildlife and economy
– Undependability of cheatgrass as a source of forage for cattle and sheep
– Reduction in native shrubs important for wildlife habitat
• Sagebrush is the main food or shelter for 170 native bird and mammal species, including sage grouse, pygmy rabbits and pronghorn antelope.
• Drop in rabbit population has secondary impact on birds of prey (e.g., bald and golden eagles)
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Pennisetum ciliare(Buffelgrass)
Pennisetum setaceum(Crimson fountaingrass)
In Hawaii, invasion of perennial grasses provides abundant fuel and increases fire frequency. This leads to dominance by more fire-tolerant non-native species.
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Impacts of buffelgrass in Arizona can be devastating on native cactus in Sonoran Desert
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Three ways fire and invasive plants interact
• Burning can lead to the establishment of new invasive species– Mainly with windblown seed (e.g., Asteraceae)
• Invasive plants can change plant communities by altering the historic fire regimes– Suppression (not common in the western US)– Promotion (very common in the western US)
• Fire can be used as a tool for the control of invasive plants
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Risks associated with prescribed burning
– Escaped fires– Air quality– Soil erosion– Effects on invasion of other non‐
desirable species– Impacts on non‐target plants– Impacts on other animals and insects
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Growth forms and life cycles• Winter annuals
– Most effective group to control, especially those that have an extended season
• Annual grasses, such as medusahead (Taeniatherum caput‐medusae), barb goatgrass (Aegilops triuncialis), ripgut brome (Bromus diandrus)
• Yellow starthistle (Centaurea solstitialis)
• Summer annuals– Generally easy to control with burning, but few invasives fall into
this category
• Biennials– Single burn events not typically effective
• Spring burn for garlic mustard (Alliaria petiolata)
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Growth forms and life cycles• Herbaceous perennials
– Few examples of success in the western US– Some success with smooth brome and Kentucky
bluegrass in east, but timing is critical• Woody plants
– Can be controlled if they do not resprout from base. If they resprout, integrated approaches need to be used
• Juniper (Juniperus spp.)• Mesquite (Prosopis spp.)
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Principles of using prescribed burning to control annual invasive plants
Reduce seedbank kill seed before they shatter understand seed longevity, germination timing and biology,
effects of fire on germination
Effects of heat on seed survival Seeds protected in some species, i.e. yellow starthistle
requires that plants be killed before seeds become viable
For annual grasses, typically need direct heat on seed seed on soil surface do not get exposed to sufficient heat to kill them in grassland fire
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Burn timing
Need enough fuel to carry a fire (or a fire with proper intensity)
Timing can also influence non‐target species Burning too early may injure desirables that have not completed their
life cycle Burning late can favor perennial grasses Burning too late may reduce invasive plant control
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How to manipulate fire intensity
– Delay grazing to build up fuels– Late afternoon fires
• not often recommended because of winds
– Backing fires compared to headfires
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Effects on other species
• Generally broadleaf species (i.e., legumes, filarees) and perennial grasses increase more than annual grasses following burning
– Native diversity generally benefits» recycles nutrients» increases solar radiation early in season, thus heating soil» reduces native pathogen under moist litter» increases light penetration to soil surface» breaks dormancy
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Centaurea solstitialis (yellow starthistle)
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Effect of consecutive burns on yellow starthistle vegetative cover
0
20
40
60
80
% V
eget
ativ
e co
ver
April July
Month of measurement
No burn 1 yr burn 2 years burn 3 years burn
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Seedbank and seedling count following 1 and 3 years of consecutive burning
Seedbank (Oct. 1995) Seedlings (March 1996)
Treatment Seeds/m2 % of unburned Seedlings/m2 % of unburned
Unburned 10,127 c* ‐‐‐‐‐ 1,328 c ‐‐‐‐‐
1995 Burn 2,673 b 26 230 b 17
1993‐1995 Burn 52 a 0.5 5 a 0.4
* different letters in columns denote statistically significant difference at the 95% confidence level
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Vegetative cover in July
0
10
20
30
40
50
60
70
80
Perc
ent V
eget
ativ
e C
over
Yellow starthistle Nassella pulchra
No burn1 yr burn3 yr burn
a a
b
b
a a
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Bromus diandrus (ripgut brome)
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19971996Bu
rned
0
20
40
60
80
100
1998
Unburned
0 20 40 60 80 100
Burn
ed
0
20
40
60
80
100 1999
Unburned
0 20 40 60 80 100
AVEfatLOTwra
EROcicTRIgra
NASpul
BRImin
AIRcar
BROhor
CENsol
BROdia
BROdia
CENsol
EROcic
AVEfat
NASpul
LACser
BROdia
CENsol
TRImic
EROcic
LACser
NASpulBROhor
NASpul
BROhor
CENsolBROdia
grass legume forb
p< 0.05
p< 0.1
n.s.
native introduced
VICsatCLApur
LATcic
SIDdip
TRImic
EPIfasCLApurLATx
TRIgra
VICvil
BROhor
VULmyuPETnan
LATcic GERdis
LACser
LOTwra
BRIminTRImic
AVEfat
LOTwra
TRIgra
BRImin
CLApur
LACser
AVEfatBRImin
Not foundon transect:CLApurEROcicLOTwraTRIgraTRImic
Kyser and DiTomaso. 2002. Weed Science 50, 648
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Aegilops triuncialis (Barb goatgrass)
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Barb goatgrass control burn
% Vegetative cover or index value
Vegetation type Unburned burn
1997 1998 1999 1997 1998 1999
Grassesbarb goatgrass 45 62 63 55 54 0
native perennials 0 0 1 1 9 10
total grasses 127 156 152 116 173 68
DiTomaso et al. 2001. Cal. Ag. 55, 47.
Pre-burn
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Burning increased the native perennial grass Hordeum brachyantherum while controlling barb goatgrass
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Taeniatherum caput‐medusae(medusahead)
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Effect of fire on medusahead control
0102030405060708090
Perc
ent M
edus
ahea
d C
over
1968 1969 1970 1971
Untreated Burned
From Young et al. 1972. J. Range Manage, 24:451
Pretreatment Burned 7/29 Burned 8/5Burned 8/7
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*
*
*
*
ModocSiskiyou
Yolo
Fresno
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Burning for medusahead control in four counties
0
20
40
60
80
100
120
140
160
% o
f un
trea
ted
cont
rol
Fresno Yolo Siskiyou Lassen
After 1 yr burn After 2 yrs burn 1 yr after last treatment
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Study site Time period Degree-days above 0 C, Oct-June
Expected frost-free days
Fresno 2001-2005 3871 238
Yolo 2001-2005 4193 265
Siskiyou 2002-2006 2365 125
Modoc 2002-2006 1992 90
XL Ranch (Young et al. 1972)
1967-1971 1791 75
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Effect of fuel load on medusahead control one year after burning
y = 76.247x - 3578.4R2 = 0.9769
0500
10001500200025003000350040004500
60 70 80 90 100
Percent reduction in medusahead cover
Fuel
bio
mas
s (lb
/A)
Lassen Co.
Siskiyou Co.
Yolo Co.
Fresno Co.
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Medusahead
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Medusahead ±97.5% CL
Flame Simulation
Percent Moisture
Second
s
012345678
42 29 9 8
LD 90LD 50
Sweet, Kyser, and DiTomaso. 2008. Invasive Plant Science and Management 1, 158
350‐500 C
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Burn window
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LD90 for the three annual grass species
Species LD90 value (seconds)
Barb goatgrass 8.0
Medusahead 4.0
Ripgut brome 1.1
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Integrated approaches that incorporate prescribed burning into management of invasive plants
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Lepidium latifolium(perennial pepperweed)
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Control of perennial pepperweed with herbicide
1. Thick layer of thatch preventing seedling establishment2. No resident vegetation to recover
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Winter Burning
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The Influence of Site Preparation Treatments and Herbicides on Perennial Grass Establishment in June 2006 (15 months after 2nd seeding)
0 10 20 30 40 50 60 70 80 90 100
Untreated
Burn
Mowing
Grazing
Tillage
Telar
Burn + Telar
Mowing + Fall Telar
Grazing + Telar
Tillage + Telar
2,4-D
Burn + 2,4-D
Mowing + Fall 2,4-D
Grazing + 2,4-D
Tillage + 2,4-D
Roundup or 2,4-D
Burn + Roundup or 2,4-D
Mowing + Fall Roundup or 2,4-D
Grazing + Roundup or 2,4-D
Tillage + Roundup or 2,4-D
% Perennial Grass Cover
Mapes Ranch
Honeylake Wildlife Area
Error bars = 95 % confidence interval
Wilson, Boelk, Kyser, and DiTomaso. Invasive Plant Science and Management 1, 17
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Yellow starthistle
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Transline (clopyralid) treated rangeland on right
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San Benito site following burn in 1999
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Yellow starthistle cover following two years of control
0102030405060708090
Bur
n/bu
rn
Bur
n/cl
opyr
Con
trol
Clo
pyr/
burn
Clo
pyr/
clop
yr
Perc
ent c
over
0
5
10
15
20
25
Bur
n/bu
rn
Bur
n/cl
opyr
Con
trol
Clo
pyr/
burn
Clo
pyr/
clop
yr
Perc
ent c
over
San Benito County Yuba County
b
aa
b
b bb
ab
c c
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02468
101214161820
Perc
ent c
over
Burn
/bur
n
Burn
/clo
pyra
lid
Con
trol
Clo
pyra
lid/b
urn
Clo
pyra
lid/c
lopy
ralid
Medusahead
05
10152025303540
Perc
ent c
over
Burn
/bur
n
Burn
/clo
pyra
lid
Con
trol
Clo
pyra
lid/b
urn
Clo
pyra
lid/c
lopy
ralid
Ripgut brome
a a
bb
cc c
cc c
Yuba County
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Yellow starthistle seedling countsSeedlings/m2
Site Treatment Untreated Treated (% untreated)
Military use2000 Burned 1999 117 271 (232%)
Clopyr. 20002001 Burn 2001 478 2 (0.4%)
2002 No treatment 363 0.8 (0.2%)
Wildland site2000 Burned 1999 435 547 (126%)
Clopyr. 20002001 Burned 2001 1560 6 (0.4%)
2002 No treatment 987 45 (5%)
Integrated management of yellow starthistle at Ft. Hunter Liggett
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Thank you!
Questions?