Yellow starthistle has become common in open areas on roadsides, rangeland, wildlands, hay fields, pastures and waste areas. It can form dense infestations that rapidly deplete soil moisture, thus preventing the establishment of other species. Effective long-term management of yellow starthistle will likely be achieved with the use of an integrated approach. This could include the use of biological control agents, mowing, prescribed burning, properly timed grazing, reseeding programs and the judicious use of herbicides.
Yellow starthistle can be controlled with a number of nonselective preemergence herbicides, including simazine, diuron, atrazine, sulfometuronmethyl, chlorsulfuron, bromacil, tebuthiuron, oxyfluorfen and prometone. All these compounds are registered for use on rights-of-way or industrial sites, but few can be used in rangeland, pastures or wildlands. In rangeland, no preemergence herbicide provides selective control of yellow starthistle without injuring desirable grasses. Chlorsulfuron is the only selective preemergence herbicide currently available that effectively controls yellow starthistle in noncrop areas, but it does not have postemergence activity on yellow starthistle and must be used in combination with 2,4-D, dicamba or triclopyr to provide some level of control.
A major problem with postemergence herbicides to control yellow starthistle (Centaurea solstitialis L.) has been the weed's ability to germinate continuously throughout winter, spring and into summer whenever moisture is available. As a result, repeated applications of broadleaf selective, postemergence herbicides such as 2,4-D, dicamba or triclopyr are required. One late application at the end of the rainy season is not sufficient because many plants are too large and are not completely controlled.
Clopyralid (Transline) is a growth-regulator herbicide that arrests development of the
growing points of the plants. It
was recently registered for use in noncrop areas of California, including
pastures, rangeland and wildlands. It
is not expected to impact the biological control agents and has been
demonstrated to be very safe on grasses but effective for the control of many
members of the sunflower family (Asteraceae), as well as legumes (Fabaceae),
nightshades (Solanaceae), and some species in the knotweed (Polygonaceae) and
carrot (Apiaceae) families. In
contrast, many other broadleaf species, including those in the mustard family (Brassicaceae)
and filarees (Erodium spp.), are
tolerant to the herbicide. Unlike
other postemergence compounds, clopyralid also has excellent preemergence
activity and is effective at very low use rates. In these experiments, we compared rates and timing of several noncrop
herbicides for yellow starthistle control, from before emergence through
Starthistle Seedling Control
We established field trials in Davis in March 1996 to compare several postemergence herbicides and the preemergence herbicide chlorsulfuron on yellow starthistle seedlings. Each plot was 5 feet by 10 feet and all treatments were applied using a CO2-pressurized backpack sprayer delivering 40 gallons per acre of spray mixture at a pressure of 20 pounds per square inch (psi). A similar experiment was also established in Davis in November 1996 to determine the most effective application timing (November to April) for control of yellow starthistle seedlings and rosettes using clopyralid, 2,4-D, triclopyr, and combinations of chlorsulfuron and 2,4-D or triclopyr. In this experiment, plots were 8 feet by 15 feet and treatments were applied using a CO2-pressurized backpack sprayer delivering 20 gallons per acre at 30 psi. All treatments in both experiments were replicated four times. Visual evaluations were used to assess percent control. Because clopyralid acts slowly on starthistle seedlings, evaluations were made at least 2 months following treatment.
Chlorsulfuron typically provides excellent postemergence and preemergence control of many weed species. However, in our first 1996 trial it gave little postemergence control of yellow starthistle, even at the highest rate, 2 ounces active ingredient per acre (oz ai/A) with or without a surfactant (Table 1). When chlorsulfuron was combined with 2,4-D or triclopyr, yellow starthistle control improved to as much as 91%. Because of the high seed production in yellow starthistle infestations, this level of control is not considered acceptable for long-term starthistle management. Application of 2,4-D in March followed by a second treatment in May controlled 96% of the yellow starthistle. Although not statistically significant, 2,4-D was consistently more effective than triclopyr. Clopyralid at the lowest rate tested in this experiment (1 oz acid equivalent/ acre, 1/6 pint product/acre) was not statistically different from repeated applications of triclopyr or 2,4-D, but consistently provided complete control of yellow starthistle for the entire season.
In a subsequent experiment, we tested clopyralid and other herbicides for yellow starthistle control every month from November 1996 through April 1997 (Table 2)). In this experiment, we used clopyralid at rates as low as 0.25 oz ae/acre (1/24 pt product/acre), which is well below the lowest registered rate of 1.5 oz ae/acre (1/4 pt product/acre). Clopyralid rates greater or equal to 1 oz ae/acre were necessary for acceptable yellow starthistle control with applications made from November through April. Although not always statistically significant, control of vellow starthistle with 1 to 6 oz ae/acre clopyralid was consistently superior to control with 2,4-D, triclopyr, and the combination of these herbicides with chlorsulfuron, in January, February and March.
These results indicate that clopyralid provides excellent control of yellow starthistle seedlings and rosettes at between 1 and 6 oz ae/acre. Furthermore, there is a wide window for application timing, extending from December through April.
To test the effectiveness of clopyralid on yellow starthistle in other Northern California regions, we conducted trials in April 1997 in Calaveras County, 5 miles north of San Andreas, and in Butte County, 7 miles north of Oroville. The Calaveras County plots were 10 feet by 10 feet and were treated identically to those in the Davis experiment. In Butte County, however, we also considered the possible effect of the previous year's starthistle skeletal remains on the efficacy of clopyralid. To test this, we established 10-feet-by-20-feet plots along a roadside heavily infested with yellow starthistle. The skeletons were mowed and removed in half of each plot, and the entire plot was treated with the appropriate rate of clopyralid as described in the previous experiment. Each trial was established as a randomized, complete block experiment with four replicates.
Calaveras County, the highest rate tested, 2 oz ae/acre, was required for
acceptable control (Table 3). We demonstrated similar results in Butte County. The control of yellow starthistle was better in the presence of skeletons
compared to the areas where skeletons were removed. With skeletal remains present, both 0.5 and 1 oz ae/acre clopyralid
provided better than 90% starthistle control. The difference between the mowed and unmowed plots was attributed to the
reduced number of seedlings present in the area shaded by the previous year's
skeletons. Consequently, fewer
seedlings were available to escape herbicide injury in the unmowed plots.
We also established a trial in the intermountain region, near Yreka (Siskiyou County) to determine the effect of clopyralid rate and treatment timing on yellow starthistle control and forage production during fall and the following spring. Plots were 10 feet by 30 feet and spray equipment was similar to that previously described. Treatments included 0.5, 1, 2 and 4 oz ae/acre clopyralid applied in every month from February through May. Both control and forage quantity were determined in October 1997, and the following spring 1998, by collecting all aboveground plant biomass in three 2.7 ft (0.25 mZ) quadrat samples per plot (four replicates per treatment) and separating uncontrolled living starthistle, dead starthistle (1997 only) and other forage species, primarily annual grasses. Data are reported as dry weight.
Poor control was obtained with 0.5 oz ae/acre clopyralid at all treatment times. In contrast, complete control of yellow starthistle was achieved in February with clopyralid rates of 1 oz ae/acre and higher (Fig. 3A). Yellow starthistle control was insufficient at 1 oz ae/acre at the late application dates, as the rosettes were larger at the time of application. Both 2 and 4 oz ae/acre clopyralid provided near complete control at all treatment timings, including the initial bolting stage in May.
Forage quantity progressively decreased with later treatment times (Fig. 3B). Desirable forage biomass was maximized with a February treatment at 4 oz ae/acre clopyralid, which represents the highest labeled Transline rate allowed in California (2/3 pt of product/acre). At this timing, yellow starthistle was in the early rosette stage. Reduced forage at later treatment times is likely due to the competitive effects of yellow starthistle on grass development during the early spring months. At higher rates, yellow starthistle injury occurred more rapidly and control was more complete, increasing light penetration and water availability to developing grasses and other desirable forage.
The following spring, yellow starthistle biomass tended to be lower with earlier application timing (Fig. 4A). Although not statistically significant, higher rates led to consistently less yellow starthistle compared with lower rates. However, this response did not appear to be due entirely to residual herbicide activity, as later application timings were not significantly different from early-season treatments. Early-season treatments also tended to increase desirable forage production compared with untreated plots and late-season treatments (Fig. 4B). Furthermore, in some cases higher rates also increased desirable forage production compared with lower rates. The early-season treatment at higher labeled rates not only provides excellent control in the year of treatment, but may also give both increased yellow starthistle control and desirable spring forage biomass 1 year after application.
Although clopyralid can effectively control yellow starthistle from December through May, the optimum timing for treatment appears to be between January and March in most locations in California. This is particularly true if the primary object of a starthistle management program is to enhance forage quality and quantity in rangeland and grassland environments.
We further compared the dose response of yellow starthistle seedlings under greenhouse conditions to several pre- and postemergence rates of clopyralid. Postemergence treatments were conducted with and without the addition of a surfactant. Ten to 20 seeds were planted in 4-inch pots. Preemergence treatments were made immediately after sowing using a compressed-air, table-spray chamber delivering 17.7 gallons per acre at 30 psi through an 8002E nozzle. After thinning to three to five seedlings per pot, postemergence applications were made to plants after two "true leaves" developed. Each treatment was replicated four times. Visual injury evaluations were used for relative comparisons between pre- and postemergence applications.
Our results indicate that the V150 (rate which caused a level of visible injury of 50% relative to untreated seedlings) for pre- and postemergence (VISO = 0.140 oz ae/acre and 0.113 oz ae/acre, respectively, without surfactant) applications were similar (fig. 3). This is supported by the wide timing window for control of starthistle seedlings under field conditions. Furthermore, the addition of an organosilicone surfactant (0.1% Sylgard) seemed to provide somewhat lower levels of yellow starthistle seedling control compared with treatments without surfactant. Two to three times more herbicide (VISo = 0.342 oz ae/acre) was required for the same level of injury when an organosilicone surfactant was added.
We conducted experiments in 1995 and 1997 to determine the most effective herbicide for late-season control of yellow starthistle. Several rates of glyphosate, triclopyr, clopyralid, 2,4-D and dicamba were applied to starthistle in the following late rosette stages: just prior to bolting (1997 only), bolting, spiny (bud) and early flowering (2% to 5% flower). Plants were treated as previously described with a minimum of 10 replicates (individual plants) per treatment in 1995 and four replicates (plots consisting of six plants each) per treatment in 1997. All treatments, except glyphosate, were applied with the addition of 0.1% Sylgard as a surfactant. Because late-season control typically occurs during the warmer spring or early summer months, amine formulations of both 2,4-D and triclopyr were used.
In 1995, we compared two rates of glyphosate and triclopyr at three stages of yellow starthistle development. Glyphosate at both rates provided excellent control at all stages (Table 4). In contrast, triclopyr provided only marginal control in the bolting stage and poor control at later growth stages. In 1997, control of late-rosette plants was excellent with all herbicides tested except for the lowest rate of glyphosate or triclopyr (Table 5). Glyphosate, dicamba, and higher rates of clopyralid and triclopyr continued to be effective when plants were in the bolting stage. At the spiny and early flowering stages, yellow starthistle plants were noticeably drought-stressed. Control was poor for all herbicides tested, regardless of the application rate. Differences between the results for glyphosate in 1995 and 1997 could be attributed to the lack of spring rainfall in 1997, compared with 1995.
If late-season yellow starthistle control is necessary, the best time to treat with glyphosate is after annual grasses or broadleaf species have completed their life cycle, but prior to yellow starthistle seed production (<5% flowering). Control is less effective when mature plants show physical signs of drought-stress. When clopyralid was previously applied in late winter or early spring, glyphosate can be used in a broadcast or spot treatment follow-up program to kill uncontrolled plants before they produce seed. It can also be used to prevent the proliferation of potential clopyralid-resistant plants. Broadcast treatment with glyphosate is not recommended when desirable perennial grasses or broadleaf species are present.
There are several advantages to using clopyralid for yellow starthistle control over other postemergence herbicides registered for use in rangeland, pastures and wildland areas. It has both pre- and postemergence activity at very low use rates, a low toxicology profile and no grazing restrictions. Treatments in December or later gave season-long control of starthistle, with earlier applications resulting in greater desirable forage production in the year of treatment, as well as the following spring. Clopyralid, glyphosate and dicamba also give effective late-season control of yellow starthistle, provided applications are not made when plants are drought-stressed.
It is important to recognize the possibility that other undesirable species, particularly annual grasses such as medusahead (Taeniatherum caputmedusae [L.] Nevski) or barbed goat-grass (Aegilops triuncialis L.), may replace yellow starthistle in clopyralid-treated areas. Under these conditions, other management strategies may be necessary. In addition, continuous clopyralid use over many years may have a long-term detrimental effect on legume populations, and potentially soil nitrogen levels. Consequently, other control options should be rotated in the overall yellow starthistle management program. Also, the potential exists for the evolution of resistance to clopyralid if the herbicide is used year after year without employing other methods. The potential for resistance can be minimized by using other strategies or through late-season applications of glyphosate to control escapes.
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