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Mech control
-hand
-tillage
-mowing
Cultural control
-grazing
-burning
-re-vegetation
Biocontrol
-insects
-biocontrol table
-plant pathogens
Chem control
- risks
--spray
--water
--toxicology
--herbicide
resist
--effects
-herbicides
--preemergence
--postemergence
--late season
--pre- & post-
--imazapic
--clopyralid
--picloram
Integrated app
Summary
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Management
Postemergence
A limited number of postemergence herbicides are registered for use in
rangelands, pastures, and wildlands. They include 2,4-D, dicamba, triclopyr
and glyphosate. These postemergent herbicide treatments generally work
best on seedlings. However, they are not effective for long-term management
of starthistle when used in spring, as they have no soil residual activity
and will not control yellow starthistle plants germinating after application.
Since yellow starthistle has the ability to germination throughout winter,
spring and into summer whenever moisture is available, achieving control
with a single application is almost impossible. A treatment following
the first flush of seedlings opens the site up for later flushes. Waiting
until later in the rainy season to apply a postemergent herbicide allows
a greater number of seedlings to be treated, but larger plants will require
higher herbicide rates and may not be controlled (DiTomaso et al. 1999c).
As a result, repeated
applications of broadleaf selective postemergence herbicides
are often necessary (DiTomaso et al. 1999b). This increases the risk of
drift to non-target species and is expensive.
Thus, the most effective way to use postemergence compounds for starthistle
control is to incorporate them into later stages of a long-term management
program. In particular, they are effectively used to spot-treat escaped
plants or to eradicate small populations in late season when starthistle
is easily visible but has yet to produce viable seed. By using spot applications
in late season, total herbicide use and expenses can be reduced because
only small sections or individual plants are treated. It is important
to note that plants should only be treated when not exposed to severe
stress. Drought stress can especially reduce the efficacy of most herbicides.
Growth regulator herbicides, including 2,4-D, dicamba and triclopyr,
will cause damage to late season broadleaf species, including desirable
natives.
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2,4-D can provide acceptable control of yellow starthistle
if it is applied at the proper rate and time. Treating plants in the
rosette growth stage provides better control than later applications.
Amine forms are as effective as ester forms at the small rosette growth
stage, and amine forms reduce the chance of off-target movement.
Application rates of 0.5 to 0.75 lb ae (acid equivalent)/acre will
control small rosettes. Applications made later in the season, when
rosettes are larger or after bolting has been initiated, require a
higher application rate (1 to 2 lb ae/acre) to achieve equivalent
control (DiTomaso et al. 1999b, Northam and Callihan 1991, Whitson
and Costa 1986) [see Tables A,
B,
C,
D].
2,4-D is a growth regulator selective herbicide and will control other
broadleaf plants, but generally will not harm grasses. It has little,
if any soil activity. Drift from 2,4-D applications is common, particularly
from the ester formulations. 2,4-D is a restricted use pesticide,
requiring a permit for use.
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Dicamba is very effective at controlling yellow starthistle
at rates as low as 0.25 lb ae/acre (Callihan and Schirman 1991). When
yellow starthistle rosettes are small, about 1 to 1.5 inches across,
the 0.25 lb ae/acre rate works well, but
higher rates (0.5 to 1.0 lb ae/acre) are needed if plants
are larger (Northam and Callihan 1991). Applications made in late
rosette to early bolting stages have provided excellent control, although
earlier treatments are better.
Dicamba is also a growth regulator selective herbicide that controls
many broadleaf plants, but generally will not harm grasses. Its soil
activity is very short. Like 2,4-D, it is also available in both an
amine and ester formulation. Drift from dicamba applications is common,
especially from the ester formulation. Dicamba is a restricted use
pesticide, requiring a permit to use.
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Triclopyr at 0.5 lb ae/acre provides fair
to complete control of yellow starthistle seedlings. Larger
plants require higher rates, up to
0.75 or
1.5 lb ae/acre (DiTomaso et al. 1999b,
Northam and Callihan 1991). Higher rates can give almost
complete control (Callihan et al. 1991), but are too expensive
and may be above labeled rates. Like 2,4-D and dicamba, triclopyr
is a growth regulator herbicide with little residual activity. It
is foliar-absorbed and active on broadleaf species, and typically
will not harm grasses. Triclopyr is formulated as both an amine and
ester. The ester formulation is more sensitive to drift than the amine
form. Triclopyr does not seem to be as effective as either dicamba
or 2,4-D on older starthistle plants.
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Glyphosate controls yellow starthistle at 1 lb ae/acre (DiTomaso
et al. 1999b). Good coverage, clean water, and actively growing yellow
starthistle plants are all essential for adequate control. Unlike
the growth regulator herbicides, glyphosate is non-selective and controls
most plants, including grasses. It has no soil activity and has an
excellent toxicoloty profile (Giesy et al. 2000). A 1% solution of
glyphosate also provides effective control and is used at this concentration
for spot treatment of small patches. Glyphosate is a very effect method
of controlling starthistle plants in the
bolting, spiny, and early flowering stages
at 1 to 2 lb ae/acre. The use of glyphosate may not be desirable in
areas where desirable perennial grasses are present unless starthistle
plants can be directly treated without contacting non-target vegetation.
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