, Australia In the late 19th century, it was introduced to temperate regions of
North America,
South America, and
Australia as an ornamental plant, and is now considered a major
agricultural and wildland noxious
weed. It has been recorded from nearly 50 countries. It is difficult to eradicate because of its drought resistance. It can spread rapidly and eventually dense stands prohibit foraging by
livestock. Infestations of cotton thistle often start in disturbed areas such as roadways, campsites, burned areas, and ditch banks. The weed adapts best to areas along rivers and streams, but can be a serious problem in pastures, grain fields and range areas. A single plant is imposing enough, but an entire colony can ruin a
pasture or destroy a park or campsite, sometimes forming tall, dense, impenetrable stands. This issue is often amplified by the prolific thorns found on this species. Besides creating an impenetrable barrier to humans and animals, the plant nearly eliminates forage use by livestock and some mammal species such as
deer and
elk. In the United States, known infestations include most of the Pacific Northwest along with Utah, Colorado, New Mexico, Wyoming, Nebraska, and South Dakota. On western rangeland, infestations directly result in significant economic losses for ranchers. It is also widespread in Australia and New Zealand. In Australia it commonly hybridises with the related invasive
Onopordum illyricum. ;Chemical Because of their shorter life cycle, cotton thistle plants can be effectively treated with herbicides. All herbicide treatments should be applied at the rosette stage of the plant. Generally, herbicide applications would be in early spring or autumn. One of the primary difficulties in chemical control of cotton thistles is their ability to germinate nearly year round. From autumn to spring a range of plant sizes can be found which may result in variable success from chemical control. Herbicides are very effective on seedlings and young rosettes, but control becomes more variable with increasing plant age.
Onopordum spp. seeds may persist for several years in the soil. Buried seed may persist for up to twenty years, and reinfestation is likely without yearly management. Therefore, several years of re-treatment may be necessary. Picloram, dicamba, 2,4-D, dicamba + 2,4,-D, and metsulfuron are effective for controlling cotton thistle. Clopyralid is more selective for controlling plants in the family Asteraceae, but will also injure or kill legumes. The
Australian painted lady butterfly has been known to use this invasive species as a host plant, but the larvae do not do enough damage to the plant for this butterfly to be used as biological control agent. In Australia, a total of seven insects have been released to control cotton thistle. Two of the seven released insects are
weevils, including
Larinus latus which feeds on the seeds, and
Lixus cardui, which bores in the stems. ;Integrated management A combination of methods (IPM) is often more effective than any single method. An
integrated pest management plan deals with prevention as well as control. Eradication of weed species is often not a practical goal, but in many cases reducing infestation to manageable levels is an achievable objective. Seed bank longevity is a major factor in managing cotton thistles. Re-establishing competitive perennial grasses and monitoring infested areas on a yearly basis is critical. Herbicides can successfully be used for reducing thistle populations and giving grasses a competitive advantage, but they cannot be used as a stand-alone solution. These techniques must be linked with good grazing practices in rangeland areas. Otherwise, the thistles will recolonize and rapidly replenish the seed bank to pre-control levels. ==References==