Fire Effects Information System (FEIS)
FEIS Home Page

Sonchus arvensis


Photographer-John M. Randall/The Nature Conservancy

Photographer-Robert W. Freckman/Wisconsin State Herbarium,

McWilliams, Jack 2004. Sonchus arvensis. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: [].


For Sonchus arvensis spp. arvensis:
    Sonchus arvensis var. arvensis [26,42,64,125].

For Sonchus arvensis spp. uliginosus:
    Sonchus uliginosus [34,58,71,127]
    Sonchus arvensis var. glabrescens [26,42,64,114,125].


field sowthistle
perennial sowthistle
perennial sow thistle

The currently accepted scientific name of field sowthistle is Sonchus arvensis L. (Asteraceae) [26,34,42,45,57,58,62,64,71,72,81,114,125,127]. There are 2 recognized subspecies:

S. arvensis subsp. arvensis
S. arvensis subsp. uliginosus (Bieb.) Nyman [45,72]

In this summary, field sowthistle will be used when discussing Sonchus arvensis, and the subspecies will be referred to by their scientific names when information pertaining to them individually is available.

Naturally occurring hybrids produced by the 2 subspecies have been detected in areas where both subspecies occur [74].


No special status

As of this writing (2004), field sowthistle is listed as a noxious weed in 13 states. More information is available through the Plants database.


SPECIES: Sonchus arvensis
Field sowthistle is of European [53,109] and western Asian [109] origin and was probably introduced into North America as a seed contaminant [75]. Sonchus arvensis spp. arvensis was first reported in 1814 in Pennsylvania [109]. The earliest collection of S. a. ssp. glabrescens in North America was from Maine in 1894. Additional collections were reported from Massachusetts and Ohio as early as 1902 [37].

Field sowthistle is reported throughout most of the United States, with the exception of Hawaii, Arizona, Oklahoma, Arkansas, Alabama, Georgia, South Carolina, and Florida. It occurs throughout Canada. Sonchus arvensis spp. arvensis has the same distribution as field sowthistle, but it is not recorded in Nebraska, Kansas, Virginia, West Virginia, North Carolina, or Alaska. Sonchus arvensis spp. uliginosus occurs across the northern portion of North America, from Alaska south to Oregon and Utah, and east to Virginia and North Carolina; but it is not reported in New Hampshire, Kentucky, British Columbia or the far northern territories of Canada [65].

No specific mention of field sowthistle in Mexico occurs in the literature. Since it occurs in Texas and New Mexico, it is reasonable to assume it may also occur in northern Mexico.

Plants database provides a state distribution map of field sowthistle and its infrataxa.

The following lists include North American ecosystems, habitat types, and forest and range cover types in which field sowthistle may occur. Field sowthistle grows well in wet and even saturated soils. Consequently, field sowthistle may occur in riparian areas or wetlands within these habitats. Additionally, field sowthistle often occurs in cultivated areas, especially small grain and row crops, so it may occur in cultivated areas within these communities, with the potential to spread into adjacent, undisturbed areas.

These lists are not necessarily inclusive or exhaustive. More information is needed to determine particular ecosystems and plant communities where field sowthistle is likely to occur in natural areas.

FRES10 White-red-jack pine
FRES11 Spruce-fir
FRES12 Longleaf-slash pine
FRES13 Loblolly-shortleaf pine
FRES14 Oak-pine
FRES15 Oak-hickory
FRES16 Oak-gum-cypress
FRES17 Elm-ash-cottonwood
FRES18 Maple-beech-birch
FRES19 Aspen-birch
FRES20 Douglas-fir
FRES21 Ponderosa pine
FRES22 Western white pine
FRES23 Fir-spruce
FRES24 Hemlock-Sitka spruce
FRES25 Larch
FRES26 Lodgepole pine
FRES27 Redwood
FRES28 Western hardwoods
FRES29 Sagebrush
FRES30 Desert shrub
FRES31 Shinnery
FRES32 Texas savanna
FRES33 Southwestern shrubsteppe
FRES34 Chaparral-mountain shrub
FRES35 Pinyon-juniper
FRES36 Mountain grasslands
FRES37 Mountain meadows
FRES38 Plains grasslands
FRES39 Prairie
FRES40 Desert grasslands
FRES41 Wet grasslands
FRES42 Annual grasslands
FRES44 Alpine

STATES/PROVINCES: (key to state/province abbreviations)



1 Northern Pacific Border
2 Cascade Mountains
3 Southern Pacific Border
4 Sierra Mountains
5 Columbia Plateau
6 Upper Basin and Range
7 Lower Basin and Range
8 Northern Rocky Mountains
9 Middle Rocky Mountains
10 Wyoming Basin
11 Southern Rocky Mountains
12 Colorado Plateau
13 Rocky Mountain Piedmont
14 Great Plains
15 Black Hills Uplift
16 Upper Missouri Basin and Broken Lands

K001 Spruce-cedar-hemlock forest
K002 Cedar-hemlock-Douglas-fir forest
K003 Silver fir-Douglas-fir forest
K004 Fir-hemlock forest
K005 Mixed conifer forest
K006 Redwood forest
K007 Red fir forest
K008 Lodgepole pine-subalpine forest
K009 Pine-cypress forest
K010 Ponderosa shrub forest
K011 Western ponderosa forest
K012 Douglas-fir forest
K013 Cedar-hemlock-pine forest
K014 Grand fir-Douglas-fir forest
K015 Western spruce-fir forest
K016 Eastern ponderosa forest
K017 Black Hills pine forest
K018 Pine-Douglas-fir forest
K020 Spruce-fir-Douglas-fir forest
K021 Southwestern spruce-fir forest
K022 Great Basin pine forest
K023 Juniper-pinyon woodland
K024 Juniper steppe woodland
K025 Alder-ash forest
K026 Oregon oakwoods
K028 Mosaic of K002 and K026
K029 California mixed evergreen forest
K030 California oakwoods
K031 Oak-juniper woodland
K032 Transition between K031 and K037
K033 Chaparral
K034 Montane chaparral
K035 Coastal sagebrush
K036 Mosaic of K030 and K035
K037 Mountain-mahogany-oak scrub
K038 Great Basin sagebrush
K039 Blackbrush
K040 Saltbush-greasewood
K041 Creosote bush
K042 Creosote bush-bur sage
K043 Paloverde-cactus shrub
K044 Creosote bush-tarbush
K045 Ceniza shrub
K047 Fescue-oatgrass
K048 California steppe
K049 Tule marshes
K050 Fescue-wheatgrass
K051 Wheatgrass-bluegrass
K052 Alpine meadows and barren
K053 Grama-galleta steppe
K054 Grama-tobosa prairie
K055 Sagebrush steppe
K056 Wheatgrass-needlegrass shrubsteppe
K057 Galleta-threeawn shrubsteppe
K058 Grama-tobosa shrubsteppe
K059 Trans-Pecos shrub savanna
K060 Mesquite savanna
K061 Mesquite-acacia savanna
K062 Mesquite-live oak savanna
K063 Foothills prairie
K064 Grama-needlegrass-wheatgrass
K065 Grama-buffalo grass
K066 Wheatgrass-needlegrass
K067 Wheatgrass-bluestem-needlegrass
K068 Wheatgrass-grama-buffalo grass
K069 Bluestem-grama prairie
K070 Sandsage-bluestem prairie
K071 Shinnery
K072 Sea oats prairie
K073 Northern cordgrass prairie
K074 Bluestem prairie
K075 Nebraska Sandhills prairie
K076 Blackland prairie
K077 Bluestem-sacahuista prairie
K078 Southern cordgrass prairie
K081 Oak savanna
K082 Mosaic of K074 and K100
K083 Cedar glades
K084 Cross Timbers
K085 Mesquite-buffalo grass
K086 Juniper-oak savanna
K087 Mesquite-oak savanna
K088 Fayette prairie
K089 Black Belt
K090 Live oak-sea oats
K093 Great Lakes spruce-fir forest
K094 Conifer bog
K095 Great Lakes pine forest
K096 Northeastern spruce-fir forest
K097 Southeastern spruce-fir forest
K098 Northern floodplain forest
K099 Maple-basswood forest
K100 Oak-hickory forest
K101 Elm-ash forest
K102 Beech-maple forest
K103 Mixed mesophytic forest
K104 Appalachian oak forest
K106 Northern hardwoods
K107 Northern hardwoods-fir forest
K108 Northern hardwoods-spruce forest
K109 Transition between K104 and K106
K110 Northeastern oak-pine forest
K111 Oak-hickory-pine
K112 Southern mixed forest
K113 Southern floodplain forest
K114 Pocosin

1 Jack pine
5 Balsam fir
12 Black spruce
13 Black spruce-tamarack
14 Northern pin oak
15 Red pine
16 Aspen
17 Pin cherry
18 Paper birch
19 Gray birch-red maple
20 White pine-northern red oak-red maple
21 Eastern white pine
22 White pine-hemlock
23 Eastern hemlock
24 Hemlock-yellow birch
25 Sugar maple-beech-yellow birch
26 Sugar maple-basswood
27 Sugar maple
28 Black cherry-maple
30 Red spruce-yellow birch
31 Red spruce-sugar maple-beech
32 Red spruce
33 Red spruce-balsam fir
34 Red spruce-Fraser fir
35 Paper birch-red spruce-balsam fir
37 Northern white-cedar
38 Tamarack
39 Black ash-American elm-red maple
40 Post oak-blackjack oak
42 Bur oak
43 Bear oak
44 Chestnut oak
45 Pitch pine
46 Eastern redcedar
50 Black locust
51 White pine-chestnut oak
52 White oak-black oak-northern red oak
53 White oak
55 Northern red oak
57 Yellow-poplar
58 Yellow-poplar-eastern hemlock
59 Yellow-poplar-white oak-northern red oak
60 Beech-sugar maple
61 River birch-sycamore
62 Silver maple-American elm
63 Cottonwood
64 Sassafras-persimmon
65 Pin oak-sweetgum
66 Ashe juniper-redberry (Pinchot) juniper
67 Mohrs (shin) oak
68 Mesquite
70 Longleaf pine
71 Longleaf pine-scrub oak
72 Southern scrub oak
73 Southern redcedar
74 Cabbage palmetto
75 Shortleaf pine
76 Shortleaf pine-oak
78 Virginia pine-oak
79 Virginia pine
80 Loblolly pine-shortleaf pine
81 Loblolly pine
82 Loblolly pine-hardwood
83 Longleaf pine-slash pine
84 Slash pine
85 Slash pine-hardwood
87 Sweetgum-yellow-poplar
88 Willow oak-water oak-diamondleaf (laurel) oak
89 Live oak
91 Swamp chestnut oak-cherrybark oak
92 Sweetgum-willow oak
93 Sugarberry-American elm-green ash
94 Sycamore-sweetgum-American elm
95 Black willow
96 Overcup oak-water hickory
97 Atlantic white-cedar
98 Pond pine
100 Pondcypress
101 Baldcypress
102 Baldcypress-tupelo
103 Water tupelo-swamp tupelo
104 Sweetbay-swamp tupelo-redbay
107 White spruce
108 Red maple
109 Hawthorn
110 Black oak
201 White spruce
202 White spruce-paper birch
203 Balsam poplar
204 Black spruce
205 Mountain hemlock
206 Engelmann spruce-subalpine fir
207 Red fir
208 Whitebark pine
209 Bristlecone pine
210 Interior Douglas-fir
211 White fir
212 Western larch
213 Grand fir
215 Western white pine
216 Blue spruce
217 Aspen
218 Lodgepole pine
219 Limber pine
220 Rocky Mountain juniper
221 Red alder
222 Black cottonwood-willow
223 Sitka spruce
224 Western hemlock
225 Western hemlock-Sitka spruce
226 Coastal true fir-hemlock
227 Western redcedar-western hemlock
228 Western redcedar
229 Pacific Douglas-fir
230 Douglas-fir-western hemlock
231 Port-Orford-cedar
232 Redwood
233 Oregon white oak
234 Douglas-fir-tanoak-Pacific madrone
235 Cottonwood-willow
236 Bur oak
237 Interior ponderosa pine
238 Western juniper
239 Pinyon-juniper
240 Arizona cypress
241 Western live oak
242 Mesquite
243 Sierra Nevada mixed conifer
244 Pacific ponderosa pine-Douglas-fir
245 Pacific ponderosa pine
246 California black oak
247 Jeffrey pine
248 Knobcone pine
249 Canyon live oak
250 Blue oak-foothills pine
251 White spruce-aspen
252 Paper birch
253 Black spruce-white spruce
254 Black spruce-paper birch
255 California coast live oak
256 California mixed subalpine

101 Bluebunch wheatgrass
102 Idaho fescue
103 Green fescue
104 Antelope bitterbrush-bluebunch wheatgrass
105 Antelope bitterbrush-Idaho fescue
106 Bluegrass scabland
107 Western juniper/big sagebrush/bluebunch wheatgrass
108 Alpine Idaho fescue
109 Ponderosa pine shrubland
110 Ponderosa pine-grassland
201 Blue oak woodland
202 Coast live oak woodland
203 Riparian woodland
204 North coastal shrub
205 Coastal sage shrub
206 Chamise chaparral
207 Scrub oak mixed chaparral
208 Ceanothus mixed chaparral
209 Montane shrubland
210 Bitterbrush
211 Creosote bush scrub
212 Blackbush
213 Alpine grassland
214 Coastal prairie
215 Valley grassland
216 Montane meadows
217 Wetlands
301 Bluebunch wheatgrass-blue grama
302 Bluebunch wheatgrass-Sandberg bluegrass
303 Bluebunch wheatgrass-western wheatgrass
304 Idaho fescue-bluebunch wheatgrass
305 Idaho fescue-Richardson needlegrass
306 Idaho fescue-slender wheatgrass
307 Idaho fescue-threadleaf sedge
308 Idaho fescue-tufted hairgrass
309 Idaho fescue-western wheatgrass
310 Needle-and-thread-blue grama
311 Rough fescue-bluebunch wheatgrass
312 Rough fescue-Idaho fescue
313 Tufted hairgrass-sedge
314 Big sagebrush-bluebunch wheatgrass
315 Big sagebrush-Idaho fescue
316 Big sagebrush-rough fescue
317 Bitterbrush-bluebunch wheatgrass
318 Bitterbrush-Idaho fescue
319 Bitterbrush-rough fescue
320 Black sagebrush-bluebunch wheatgrass
321 Black sagebrush-Idaho fescue
322 Curlleaf mountain-mahogany-bluebunch wheatgrass
323 Shrubby cinquefoil-rough fescue
324 Threetip sagebrush-Idaho fescue
401 Basin big sagebrush
402 Mountain big sagebrush
403 Wyoming big sagebrush
404 Threetip sagebrush
405 Black sagebrush
406 Low sagebrush
407 Stiff sagebrush
408 Other sagebrush types
409 Tall forb
410 Alpine rangeland
411 Aspen woodland
412 Juniper-pinyon woodland
413 Gambel oak
414 Salt desert shrub
415 Curlleaf mountain-mahogany
416 True mountain-mahogany
417 Littleleaf mountain-mahogany
418 Bigtooth maple
419 Bittercherry
420 Snowbrush
421 Chokecherry-serviceberry-rose
422 Riparian
501 Saltbush-greasewood
502 Grama-galleta
503 Arizona chaparral
504 Juniper-pinyon pine woodland
505 Grama-tobosa shrub
506 Creosotebush-bursage
507 Palo verde-cactus
508 Creosotebush-tarbush
509 Transition between oak-juniper woodland and mahogany-oak association
601 Bluestem prairie
602 Bluestem-prairie sandreed
603 Prairie sandreed-needlegrass
604 Bluestem-grama prairie
605 Sandsage prairie
606 Wheatgrass-bluestem-needlegrass
607 Wheatgrass-needlegrass
608 Wheatgrass-grama-needlegrass
609 Wheatgrass-grama
610 Wheatgrass
611 Blue grama-buffalo grass
612 Sagebrush-grass
613 Fescue grassland
614 Crested wheatgrass
615 Wheatgrass-saltgrass-grama
701 Alkali sacaton-tobosagrass
702 Black grama-alkali sacaton
703 Black grama-sideoats grama
704 Blue grama-western wheatgrass
705 Blue grama-galleta
706 Blue grama-sideoats grama
707 Blue grama-sideoats grama-black grama
708 Bluestem-dropseed
709 Bluestem-grama
710 Bluestem prairie
711 Bluestem-sacahuista prairie
712 Galleta-alkali sacaton
713 Grama-muhly-threeawn
714 Grama-bluestem
715 Grama-buffalo grass
716 Grama-feathergrass
717 Little bluestem-Indiangrass-Texas wintergrass
718 Mesquite-grama
719 Mesquite-liveoak-seacoast bluestem
720 Sand bluestem-little bluestem (dunes)
721 Sand bluestem-little bluestem (plains)
722 Sand sagebrush-mixed prairie
723 Sea oats
724 Sideoats grama-New Mexico feathergrass-winterfat
725 Vine mesquite-alkali sacaton
726 Cordgrass
727 Mesquite-buffalo grass
728 Mesquite-granjeno-acacia
729 Mesquite
730 Sand shinnery oak
731 Cross timbers-Oklahoma
732 Cross timbers-Texas (little bluestem-post oak)
733 Juniper-oak
734 Mesquite-oak
735 Sideoats grama-sumac-juniper
801 Savanna
802 Missouri prairie
803 Missouri glades
804 Tall fescue
805 Riparian
806 Gulf Coast salt marsh
807 Gulf Coast fresh marsh
901 Alder
902 Alpine herb
903 Beach wildrye-mixed forb
904 Black spruce-lichen
905 Bluejoint reedgrass
906 Broadleaf forest
907 Dryas
908 Fescue
909 Freshwater marsh
910 Hairgrass
911 Lichen tundra
912 Low scrub shrub birch-ericaceous
913 Low scrub swamp
914 Mesic sedge-grass-herb meadow tundra
915 Mixed herb-herbaceous
916 Sedge-shrub tundra
917 Tall shrub swamp
918 Tussock tundra
919 Wet meadow tundra
920 White spruce-paper birch
921 Willow

Field sowthistle is found in a wide range of habitats. It occurs in cultivated fields of both small grains and row crops, in disturbed areas, "waste grounds," meadows, sloughs, woods, lawns, and along roadsides, beaches, ditches, and river and lake shores [109,110]. Although field sowthistle is adapted to many habitats, it is mentioned most often in the literature in relation to saline habitat types.

Field sowthistle is found on disturbed sites in saline habitats in Saskatchewan, Manitoba, and Alberta in association with rayless alkali aster (Symphyotrichum ciliatum), spear saltbush (Atriplex patula), curlycup gumweed (Grindelia squarrosa), summer-cypress (Kochia scoparia), Nuttall's alkaligrass (Puccinellia nuttalliana), red swampfire (Salicornia rubra), and Pursh seepweed (Suaeda calceoliformis) [16].

Major species associated with S. a. ssp. uliginosus in halophytic or semihalophytic communities in Saskatchewan near saline depressions include western yarrow (Achillea millefolium), rosy pussytoes (Antennaria microphylla), manyflowered aster (Symphyotrichum ericoides var. pansum), saltgrass (Distichlis spicata), wild licorice (Glycyrrhiza lepidota), foxtail barley (Hordeum jubatum), mat muhly (Muhlenbergia richardsonis), and gray goldenrod (Solidago nemoralis) [33].

Redmann [98] described plant communities along a soil salinity-moisture gradient of an eastern North Dakota prairie. Field sowthistle was present in every plant community except the muhly (Muhlenbergia spp.) and bluestem (Andropogon spp.) types. In a prairie cordgrass (Spartina pectinata) community, field sowthistle commonly occurs with foxtail barley, slender wheatgrass (Elymus trachycaulus), scratchgrass (M. asperifolia), mat muhly, bluejoint reedgrass (Calamagrostis canadensis), northern bog aster (Symphyotrichum boreale), and marsh hedgenettle (Stachys palustris). In a bluegrass (Poa spp.) community type, field sowthistle occurs at lower elevations with foxtail barley, scratchgrass, wild licorice, and Maximilian sunflower (Helianthus maximiliani). Sonchus arvensis ssp. uliginosus is found in a "salt flat" area, or saltgrass community type, with saltgrass, serpentine aster (Symphyotrichum ericoides), curlycup gumweed, alkali cordgrass (Spartina gracilis), foxtail barley, slender wheatgrass, scratchgrass, and plains bluegrass (Poa arida). It is also found in the foxtail barley community type where it occurs with plains bluegrass, scratchgrass, curlycup gumweed, serpentine aster, curly dock (Rumex crispus), prairie wedgescale (Sphenopholis obtusata), and Cuman ragweed (Ambrosia psilostachya) [98].


SPECIES: Sonchus arvensis
The following description of field sowthistle provides characteristics that may be relevant to fire ecology, and is not meant for identification. Keys for identification are available in these sources: [26,34,42,45].

Field sowthistle is a perennial herb [53,74] that reproduces by seeds, by vertical, thickened roots, and by cylindrical, horizontal, spreading roots [110]. Vertical roots can penetrate 5 to10 feet (1.5-3  m) deep. Horizontal roots, frequently 2.5 to 5 mm in diameter (rarely exceeding 10 mm), are found 2 to 4 inches (5-10 cm) below the soil surface [10]. These horizontal roots can reach 3 to 6 feet (0.9-1.8 m) in length in a single growing season [110]. Fruits are achenes [15,90] with a pappus that generally stays attached to the achene [92].

Stems are erect, 0.1 to 0.4 inches (3-10 mm) in diameter, and most commonly 24 to 59 inches (60-150 cm) tall; although they range from 12 to 71 inches (30-180 cm) tall. Stems are hollow and branched, varying from 2 to many per plant. Leaves are crowded on the lower stems and sparse on the upper stems. The entire plant is filled with milky latex [74].


Field sowthistle can reproduce by seed and vegetatively [10,30,110].

Breeding system: Field sowthistle flowers are perfect [31] and generally self-incompatible [31,110].

Pollination: Field sowthistle is pollinated by insects including honeybees and other bees, hover flies, and blister beetles [31,110].

Seed production: Field sowthistle can produce large numbers of seeds [31,53,110,112]. Seeds produced by self pollination are generally nonviable and smaller than those produced by cross-pollination [31,110].

Heads contain many fertile flowers but the number of achenes produced varies widely among heads, plants, and locality. Variability likely results from several factors, including environmental conditions and availability of pollinators [110].

Field sowthistle can typically produce an average of 30 achenes per head and up to 50,000/yd2 [110]. In North Dakota, 1 main stalk, with "relatively little competition", produced 62 heads and 9,750 well-developed achenes. The author collected seeds from the plant for a 30-day period [112]. In South Dakota, artificially cross-pollinated heads from greenhouse- and field-grown plants produced about 50 achenes per head, but number of achenes per head in natural populations varied from about 20 to 40 or from 60 to 80, depending upon the year [31].

Seed dispersal: Seeds of field sowthistle are mostly wind dispersed [28,53,110], but other dispersal agents may play a minor role. The pappus, attached to the seed, aids in wind dispersal [92]. Hume and Archibold [63] placed seed traps at varying distances from a "weedy" field in Saskatchewan. Results show wind-blown seeds of field sowthistle can disperse at least 110 yards (100 m). They do not report wind speed.

Sheldon and Burrows [105] conducted experiments to determine maximum dispersal distance of field sowthistle seeds at differing wind speeds. They used field sowthistle plants with a mean height of 3 feet (90 cm). They observed a maximum dispersal distance of 11 yards (10 m).

Wind speed (km/hour) 5.47 10.94 16.41
Dispersal distance (m) 3.34 6.67 10.00

In addition to wind dispersal, seeds of field sowthistle may be dispersed by birds and other animals. Martin and others (as reported in [133], a literature review) state field sowthistle is a minor element in the diet of some North American birds, and some seeds may germinate after ingestion and excretion by birds and animals. Hooked cells at the tips of pappus hairs allow the pappus to cling to clothes and animal hairs and aid in seed dispersal [110,133].

Seed banking: While viable field sowthistle seeds have been found in the seed banks of marshes and wetlands [60,88], longevity of seeds in the soil seed bank under field conditions of these communities is unknown. A study of field sowthistle seed dormancy suggests that some seed may remain viable for 3 or more years in cultivated soils [23].

Seed banking studies in the Delta Marsh, Manitoba, suggest that viable field sowthistle seeds occur in marsh habitats. Sowthistles (Sonchus spp.) were dominant in the drier upland areas, so seed was likely dispersed throughout the marsh. Field sowthistle seedlings emerged from soil samples taken from the marsh and exposed to "drawdown" conditions (soil surface kept moist), but not from samples exposed to "submersed" conditions (continuously flooded to a depth of 2 to 3 cm above the soil surface) [88].

In an experiment designed to test seedling emergence from boreal wetland soils under changing climatic conditions, field sowthistle seedlings emerged from the soil seed bank in willow (Salix spp.) savanna and bluejoint reedgrass vegetation zones of a mid-boreal wetland in Alberta [60].

Although seeds of field sowthistle have low viability in cultivated fields, some can remain dormant but viable for more than 3 years in cultivated soil. Chepil [23] conducted 3 separate seed dormancy tests for "weed" species in cultivated soil in Saskatchewan. In the 1st experiment an indefinite number of field sowthistle seeds was planted in 3 soil types on 18 September, 1937. Introduction of seeds from other sources was prevented. No seeds were planted greater than 3 inches (7.6 cm) deep. Number of viable seeds remaining in the soil after 3 years was determined by repeated germination tests in the laboratory until no more germination occurred. Results are shown in the table below [23]:

Percentage of field sowthistle seeds germinated each year after planting in 3 soil types in 1937 [23]
Soil texture 1938 1939 1940 Viable seeds remaining
Clay 43.3 16.2 2.7 37.8
Loam 66.7 13.3 0 20.0
Sandy loam 86.7 0 3.3 10.0

In the 2nd experiment, 50 field sowthistle seeds were planted no deeper than 3 inches (7.6 cm) on 14 October, 1938, in 3 soil types. Again, number of viable seeds remaining in the soil after 6 years was determined by repeated germination tests in the laboratory until no more germination occurred. Values given are number of viable seeds [23].

Soil texture 1939 1940 1941 1942 1943 1944 Viable seeds remaining
Clay 33 0 4 0 0 0 0
Loam 1 0 0 0 0 0 0
Sandy loam 2 3 0 0 0 0 1

The 3rd experiment utilized 1,000 field sowthistle seeds planted no deeper than 3 inches (7.6 cm). Seeds were planted between 1 and 5 November, 1940, in 3 soil types and only seeds germinated in the field were counted. Numbers are actual seeds germinating, not percentages [23].

Soil texture 1941 1942 1943 1944 1945
Clay 18 0 2 5 0
Loam 16 0 0 0 0
Sandy loam 12 0 0 1 0

Clay appears to be most conducive to long-term viability of field sowthistle seeds [23] (See Site Characteristics).

Germination: Germination of field sowthistle seeds increases with both increasing soil temperature and time since flowering. Field sowthistle seed in the field begins to germinate when the soil has "warmed" [74].

Seeds may be capable of germination about 5 days after pollination [74]; however, germination rates increased from low to none 4 days after flowering to a maximum 7 to 9 days after flowering [31,66,110]. In field germination experiments in South Dakota, Derscheid and Schultz [31] noted that percentage of viable seeds produced by field sowthistle ranged from 10% 6 days after blooming to 89% 9 days after blooming. If field sowthistle plants are pulled or cut and placed in a pile it is possible for viable seeds to be produced if flowers are present when the plants are cut [110].

In laboratory germination tests, field sowthistle seed viability is "relatively" high. Kinch and Termunde [66] achieved 95% germination in the laboratory using "well-matured" seed.

Orientation of field sowthistle seeds in the soil profile is important to germination, and light may stimulate germination. Bosy and Aarssen [15] conducted seed germination tests on field sowthistle using agar as a germinating medium. Agar was used to eliminate any environmental differences at a given depth and enabled the authors to maintain seed orientation. They found surface-lying seeds of field sowthistle displayed higher germination than buried seeds [15]. Germination was 50% for seeds germinated in soil and 80% for seeds germinated on moist filter paper, and germination was higher in diffuse laboratory light than in complete darkness [90]. When seeds were buried, seeds oriented with the radicle horizontal had significantly greater (P<0.05) germination than seeds with the radicle oriented either upward or downward.

Studies indicate temperatures from 77 to 86 °F (25-30 °C) are optimal for germination. Seeds germinate poorly (<5%) below 68 °F (20 °C) and above 95 °F (35 °C), but alternating temperatures were more favorable for germination than constant temperatures if temperatures above 77 °F (25 °C) are included in the cycle [52]. Stevens [110] reports seeds exposed to 90 °F (32 °C) for a "few hours daily" germinate "freely" in 4 to 7 days.

Field sowthistle seed germination in wetlands could be limited by saturated soils. For example, Hogenbirk and Wein [60] germinated seeds of field sowthistle from combined soil and litter samples from a mid-boreal wetland in Alberta. No field sowthistle seeds germinated in samples taken from a sedge (Carex spp.) marsh. Field sowthistle seeds stored in fresh water were 100% decomposed after 3 months storage [18].

Seedling establishment/growth: Field sowthistle seedlings survive best in areas with protective plant cover or litter and high moisture compared with open cultivated soil [110]. Accordingly, seedlings are often only found along pond, ditch, or field margins, or in lawns, meadows, or uncultivated fields [92]. In a series of field germination experiments with field sowthistle seeds, Stevens [110] had little success growing seedlings in cultivated field plots. Laboratory germination tests with the same lot of seeds showed 56% germination.

Most field sowthistle seedlings do not emerge until mid- to late May in Saskatchewan and the Great Plains of the United States [74]. Seedlings grow slowly for about the first 2 weeks until leaves are about 1.2 inches (3 cm) long [110]. They develop rapidly after that, and reproductive ability of spreading roots is established quickly [52,110]. Stevens [110] noted 10 seedlings on 17 May, 1923. The 10 seedlings grew slowly until 1 June when the largest leaves were 1.2 inches (3 cm) long. After that, they developed "rapidly" and on 5 July, a horizontal root 28 inches long (71 cm) was removed from the largest plant [110].

Most seedlings do not flower the first year, but flowering in late summer is possible from some first-year seedlings in favorable environments [52,110].

Asexual regeneration: Field sowthistle reproduces vegetatively from buds on horizontal and vertical roots and on basal portions of aerial stems located just under the soil surface. Thickened roots develop as a result of secondary growth of original fibrous roots [51] and begin to show reproductive capacity when thickened to 1 to 1.5 mm [50]. This occurs on vertical primary roots when seedlings reach the 4-leaf stage and on horizontal roots when seedlings have 6 to 7 photosynthetic leaves. One-month-old seedlings can have 7 to 8 leaves with horizontal roots from 4 to 6 inches (10-15 cm) long and 1.5 mm thick. Horizontal roots from 24 to 39 inches (60-100 cm) and vertical roots penetrating 20 inches (50 cm) can develop from seedlings within 4 months after emergence. Vertical roots can produce vegetative buds as deep as 20 inches (50 cm) below the soil surface, and new aerial growth has been observed from buds as deep as 16 inches (40 cm) below the soil surface [110]. New shoots can develop from buds that overwinter on both vertical and horizontal "spreading" roots, and/or on basal portions of aerial stems [51,89]. In North Dakota, the rate of vegetative spread of field sowthistle clones varied from 1.6 to 9 feet (0.5-2.8 m) per year, depending on the clone (personal observation in [74]).

Harris and Shorthouse [53] describe the horizontal roots of field sowthistle as "easily broken", and new plants can grow from root fragments and flower within 1 year [50,110]. Of field sowthistle root fragments planted on 3 May in a field experiment in North Dakota, approximately 50% of 0.25-inch-long pieces, 75% of 0.5-inch-long pieces, and 85% of 1-inch-long pieces produced plants within 20 to 34 days. Where well developed buds were present on root fragments, plants emerged quickly and were strong; if buds were not present, new plants grew more slowly from the cut surface and were weak. Plants grown from these root fragments reached a height of 3 feet (1 m) and flowered abundantly between 27 July and 6 August. On 29 June the largest of these plants had 2 horizontal roots 42 to 45 inches long (107-114 cm). The 45-inch root had 42 buds and sprouts in various stages of development. By the end of the growing season, horizontal roots from these plants reached about 6 feet (1.8 m) in length [110].

Field sowthistle is adapted to moist, sunny locations in temperate regions but is absent from tropical areas [74]. Within temperate regions, field sowthistle has a broad tolerance to variable environments and adapts well to wet sites, even with little soil disturbance. In Canada, field sowthistle occurs in areas that receive average annual precipitation of 12 to 120 inches (300-3,000 mm) [133]. In a greenhouse study, growth of field sowthistle plants was positively correlated with increasing soil water, with greatest growth occurring at complete saturation [132]. However, field sowthistle also establishes on dry sites [98]. Neither the climatic conditions required for successful establishment nor conditions, if any, favoring S. a. ssp. arvensis over S. a. ssp. uliginosus have been established [74].

Field sowthistle is adapted to many soil types but appears to prefer fine-textured soils and does not thrive on dry, coarse-textured sand. Field sowthistle seems to prefer slightly alkaline or neutral soils and does not thrive in acid soils, salt marshes, or highly alkaline areas [110]. However, Zollinger and Kells [132] determined soil pH had little effect on leaf production, plant height, or number of capitula produced.

Field sowthistle is present in a variety of community types from those occurring on wet, very strongly saline surface soil and strongly saline subsoil to nonsaline and dry soils [98]. Dodd and Coupland [33] describe field sowthistle as occurring in halophytic or semihalophytic communities in Saskatchewan.

Field sowthistle is an early-successional plant. Komarova [67] and Zollinger and Parker [133] describe field sowthistle as a pioneer species. In a study of succession after fire in "highland hardwoods" in Wisconsin, it appeared in 6 out of 10 plots in the herbaceous stage of succession [44]. Although infrequent, field sowthistle is part of the early successional community on wetlands in the blast zone after the Mount St. Helen's eruption [121].

Field sowthistle is most competitive under abundant precipitation and moderate climates [133].

Shoots and new roots in established stands begin to develop when the soil starts to warm [51,110]. Small leaves begin to appear from shallow roots about 1 week from initial growth [110], and adventitious root development begins 3 to 4 weeks later. Initial thickening of new roots begins when plants have 5 to 7 leaves [50,52]. Secondary thickening proceeds quickly, and spreading roots 4 mm thick and over 79 inches (200 cm) long can be detected by 3 months after initial growth [110]. Thickening of new roots ceases by mid-summer. New shoots develop from roots 2-3 mm in diameter until late summer [74].

Flowering stems begin to develop when plants have 12 to 15 leaves [50,110]. Flowering begins about 1 July in the northern United States and continues until plants are frosted, although most flowering is complete by late summer [110]. Time required from flowering to fruit maturation is about 10 days [74].


SPECIES: Sonchus arvensis
Fire adaptations: As of this writing (2004), no information is available specifically addressing fire adaptations in field sowthistle; however, inferences regarding its ability to establish, persist, and spread after fire are possible, based on its regeneration strategies and data from a small number of fire studies in which field sowthistle occurred.

Field sowthistle seeds are dispersed by wind (see Seed dispersal), and seedlings may establish on burned areas from offsite seed sources when mature plants occur in the vicinity of the burn. Seedlings established on burned sites in red pine forest in Minnesota [3] and on the Delta Marsh in Manitoba [120], while no field sowthistle plants occurred on unburned control plots in either study. Probability of postfire establishment from offsite seed may be related to season of burning (see Plant Response to Fire). Information on seed banking for field sowthistle suggests that it is possible for seedlings to establish from the soil seed bank after fire, although this has not been documented in the available literature.

Field sowthistle plants are likely to survive and persist on burned areas, even after high-severity fire, and the limited available data on postfire response of field sowthistle indicate little difference in abundance between burned and unburned sites [59,86] (see Plant response to fire). Field sowthistle shoots develop from numerous underground buds on both vertical and horizontal roots, and on basal portions of aerial stems [51,89] (see Asexual regeneration). Vertical roots can be 5 to 10 feet (1.5-3 m) deep [10] with the potential to produce shoots from buds as deep as 16 inches (40 cm) below the soil surface [110]. These buds would not be affected by fire. Horizontal roots of field sowthistle occur 2 to 4 inches (5-10 cm) below the surface [10] and would probably also be protected from all but the most severe fires.

Fire regimes: As of this writing (2004), no information regarding fire regimes in which field sowthistle evolved was found in the available literature; nor was information available regarding impacts of field sowthistle invasion on fuel characteristics or fire regimes in native North American plant communities. The following table provides fire return intervals for plant communities and ecosystems where field sowthistle may occur in North America. Field sowthistle may also occur within riparian or wetland areas included in these ecosystems. Find further fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find Fire Regimes".

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
silver fir-Douglas-fir Abies amabilis-Pseudotsuga menziesii var. menziesii > 200
grand fir Abies grandis 35-200 [6]
maple-beech-birch Acer-Fagus-Betula > 1,000
silver maple-American elm Acer saccharinum-Ulmus americana < 35 to 200
sugar maple Acer saccharum > 1,000
sugar maple-basswood Acer saccharum-Tilia americana > 1,000 [126]
California chaparral Adenostoma and/or Arctostaphylos spp. < 35 to < 100 [87]
bluestem prairie Andropogon gerardii var. gerardii-Schizachyrium scoparium < 10 [68,87]
Nebraska sandhills prairie Andropogon gerardii var. paucipilus-Schizachyrium scoparium < 10
bluestem-Sacahuista prairie Andropogon littoralis-Spartina spartinae < 10 [87]
silver sagebrush steppe Artemisia cana 5-45 [56,96,130]
sagebrush steppe Artemisia tridentata/Pseudoroegneria spicata 20-70 [87]
basin big sagebrush Artemisia tridentata var. tridentata 12-43 [101]
mountain big sagebrush Artemisia tridentata var. vaseyana 15-40 [8,22,80]
Wyoming big sagebrush Artemisia tridentata var. wyomingensis 10-70 (40**) [124,131]
coastal sagebrush Artemisia californica  
saltbush-greasewood Atriplex confertifolia-Sarcobatus vermiculatus  
desert grasslands Bouteloua eriopoda and/or Pleuraphis mutica 5-100 [87]
plains grasslands Bouteloua spp. < 35 [87,130]
blue grama-needle-and-thread grass-western wheatgrass Bouteloua gracilis-Hesperostipa comata-Pascopyrum smithii < 35 [87,100,130]
blue grama-buffalo grass Bouteloua gracilis-Buchloe dactyloides < 35 [87,130]
grama-galleta steppe Bouteloua gracilis-Pleuraphis jamesii < 35 to < 100
blue grama-tobosa prairie Bouteloua gracilis-Pleuraphis mutica < 35 to < 100 [87]
cheatgrass Bromus tectorum < 10 [95,128]
California montane chaparral Ceanothus and/or Arctostaphylos spp. 50-100 [87]
sugarberry-America elm-green ash Celtis laevigata-Ulmus americana-Fraxinus pennsylvanica < 35 to 200 [126]
paloverde-cactus shrub Cercidium microphyllum/Opuntia spp. < 35 to < 100 [87]
curlleaf mountain-mahogany* Cercocarpus ledifolius 13-1,000 [9,103]
mountain-mahogany-Gambel oak scrub Cercocarpus ledifolius-Quercus gambelii < 35 to < 100 [87]
Atlantic white-cedar Chamaecyparis thyoides 35 to > 200 [126]
blackbrush Coleogyne ramosissima < 35 to < 100
Arizona cypress Cupressus arizonica < 35 to 200
northern cordgrass prairie Distichlis spicata-Spartina spp. 1-3 [87]
beech-sugar maple Fagus spp.-Acer saccharum > 1,000 [126]
California steppe Festuca-Danthonia spp. < 35 [87,115]
black ash Fraxinus nigra < 35 to 200
juniper-oak savanna Juniperus ashei-Quercus virginiana < 35
Ashe juniper Juniperus ashei < 35
western juniper Juniperus occidentalis 20-70
Rocky Mountain juniper Juniperus scopulorum < 35 [87]
cedar glades Juniperus virginiana 3-22 [49,87]
tamarack Larix laricina 35-200 [87]
western larch Larix occidentalis 25-350 [13,29]
creosotebush Larrea tridentata < 35 to < 100
Ceniza shrub Larrea tridentata-Leucophyllum frutescens-Prosopis glandulosa < 35 [87]
yellow-poplar Liriodendron tulipifera < 35 [126]
wheatgrass plains grasslands Pascopyrum smithii < 5-47+ [87,96,130]
Great Lakes spruce-fir Picea-Abies spp. 35 to > 200
northeastern spruce-fir Picea-Abies spp. 35-200 [35]
southeastern spruce-fir Picea-Abies spp. 35 to > 200 [126]
Engelmann spruce-subalpine fir Picea engelmannii-Abies lasiocarpa 35 to > 200 [6]
black spruce Picea mariana 35-200
conifer bog* Picea mariana-Larix laricina 35-200 [35]
blue spruce* Picea pungens 35-200 [6]
red spruce* Picea rubens 35-200 [35]
pine-cypress forest Pinus-Cupressus spp. < 35 to 200 [6]
pinyon-juniper Pinus-Juniperus spp. < 35 [87]
whitebark pine* Pinus albicaulis 50-200 [2,4]
jack pine Pinus banksiana <35 to 200 [35]
Mexican pinyon Pinus cembroides 20-70 [82,117]
Rocky Mountain lodgepole pine* Pinus contorta var. latifolia 25-340 [12,13,119]
Sierra lodgepole pine* Pinus contorta var. murrayana 35-200 [6]
shortleaf pine Pinus echinata 2-15
shortleaf pine-oak Pinus echinata-Quercus spp. < 10 [126]
Colorado pinyon Pinus edulis 10-400+ [39,43,87]
slash pine Pinus elliottii 3-8
slash pine-hardwood Pinus elliottii-variable < 35 [126]
Jeffrey pine Pinus jeffreyi 5-30
western white pine* Pinus monticola 50-200 [6]
longleaf-slash pine Pinus palustris-P. elliottii 1-4 [85,126]
longleaf pine-scrub oak Pinus palustris-Quercus spp. 6-10 [126]
Pacific ponderosa pine* Pinus ponderosa var. ponderosa 1-47 [6]
interior ponderosa pine* Pinus ponderosa var. scopulorum 2-30  [6,11,73]
Arizona pine Pinus ponderosa var. arizonica 2-15 [11,25,104]
Table Mountain pine Pinus pungens < 35 to 200 [126]
red pine (Great Lakes region) Pinus resinosa 10-200 (10**) [35,40]
red-white-jack pine* Pinus resinosa-P. strobus-P. banksiana 10-300 [35,54]
pitch pine Pinus rigida 6-25 [21,55]
pocosin Pinus serotina 3-8
pond pine Pinus serotina 3-8
eastern white pine Pinus strobus 35-200
eastern white pine-eastern hemlock Pinus strobus-Tsuga canadensis 35-200
eastern white pine-northern red oak-red maple Pinus strobus-Quercus rubra-Acer rubrum 35-200
loblolly pine Pinus taeda 3-8
loblolly-shortleaf pine Pinus taeda-P. echinata 10 to < 35
Virginia pine Pinus virginiana 10 to < 35
Virginia pine-oak Pinus virginiana-Quercus spp. 10 to < 35
sycamore-sweetgum-American elm Platanus occidentalis-Liquidambar styraciflua-Ulmus americana < 35 to 200 [126]
galleta-threeawn shrubsteppe Pleuraphis jamesii-Aristida purpurea < 35 to < 100
eastern cottonwood Populus deltoides < 35 to 200 [87]
aspen-birch Populus tremuloides-Betula papyrifera 35-200 [35,126]
quaking aspen (west of the Great Plains) Populus tremuloides 7-120 [6,47,79]
mesquite Prosopis glandulosa < 35 to < 100 [78,87]
mesquite-buffalo grass Prosopis glandulosa-Buchloe dactyloides < 35
Texas savanna Prosopis glandulosa var. glandulosa < 10
black cherry-sugar maple Prunus serotina-Acer saccharum > 1,000 [126]
mountain grasslands Pseudoroegneria spicata 3-40 (10**) [5,6]
Rocky Mountain Douglas-fir* Pseudotsuga menziesii var. glauca 25-100 [6,7,8]
coastal Douglas-fir* Pseudotsuga menziesii var. menziesii 40-240  [6,83,99]
California mixed evergreen Pseudotsuga menziesii var. menziesii-Lithocarpus densiflorus-Arbutus menziesii < 35
California oakwoods Quercus spp. < 35 Arno00 [6]
oak-hickory Quercus-Carya spp. < 35 [126]
oak-juniper woodland (Southwest) Quercus-Juniperus spp. < 35 to < 200 [87]
northeastern oak-pine Quercus-Pinus spp. 10 to < 35 [126]
oak-gum-cypress Quercus-Nyssa-spp.-Taxodium distichum 35 to > 200 [85]
southeastern oak-pine Quercus-Pinus spp. < 10 [126]
coast live oak Quercus agrifolia 2-75 [46]
white oak-black oak-northern red oak Quercus alba-Q. velutina-Q. rubra < 35 [126]
canyon live oak Quercus chrysolepis <35 to 200
blue oak-foothills pine Quercus douglasii-P. sabiniana <35 [6]
northern pin oak Quercus ellipsoidalis < 35 [126]
Oregon white oak Quercus garryana < 35 [6]
bear oak Quercus ilicifolia < 35 [126]
California black oak Quercus kelloggii 5-30 [87]
bur oak Quercus macrocarpa < 10 [126]
oak savanna Quercus macrocarpa/Andropogon gerardii-Schizachyrium scoparium 2-14 [87,126]
shinnery Quercus mohriana < 35 [87]
chestnut oak Quercus prinus 3-8
northern red oak Quercus rubra 10 to < 35
post oak-blackjack oak Quercus stellata-Q. marilandica < 10
black oak Quercus velutina < 35
live oak Quercus virginiana 10 to< 100 [126]
interior live oak Quercus wislizenii < 35 [6]
cabbage palmetto-slash pine Sabal palmetto-Pinus elliottii < 10 [85,126]
blackland prairie Schizachyrium scoparium-Nassella leucotricha < 10
Fayette prairie Schizachyrium scoparium-Buchloe dactyloides < 10 [126]
little bluestem-grama prairie Schizachyrium scoparium-Bouteloua spp. < 35
tule marshes Scirpus and/or Typha spp. < 35 [87]
redwood Sequoia sempervirens 5-200 [6,38,116]
southern cordgrass prairie Spartina alterniflora 1-3 [87]
baldcypress Taxodium distichum var. distichum 100 to > 300
pondcypress Taxodium distichum var. nutans < 35 [85]
western redcedar-western hemlock Thuja plicata-Tsuga heterophylla > 200 [6]
eastern hemlock-yellow birch Tsuga canadensis-Betula alleghaniensis > 200 [126]
western hemlock-Sitka spruce Tsuga heterophylla-Picea sitchensis > 200
mountain hemlock* Tsuga mertensiana 35 to > 200 [6]
elm-ash-cottonwood Ulmus-Fraxinus-Populus spp. < 35 to 200 [35,126]
*fire return interval varies widely; trends in variation are noted in the species review

Geophyte, growing points deep in soil
Ground residual colonizer (on-site, initial community)
Initial off-site colonizer (off-site, initial community)


SPECIES: Sonchus arvensis
As of this writing (2004), no accounts in the literature discuss or describe immediate effects of fire on field sowthistle plants or seeds. It is reasonable to assume that field sowthistle plants are top-killed by fire and that some underground regenerating organs survive even high-severity fire (see Fire adaptations).

No additional information is available on this topic.

Field sowthistle can establish on burned sites from wind-dispersed seed, as suggested by results of studies in red pine (Pinus resinosa) forest in Minnesota [3] and on the Delta Marsh in Manitoba [120]. Field sowthistle seedlings may be more likely to establish on burned sites after summer fires, when field sowthistle plants are likely to be dispersing seed, than following fall or spring fires [120].

Established field sowthistle plants are likely to persist after fire on burned sites, though it is unclear whether its overall abundance will increase or decrease in the postfire environment. Postfire data from studies in Alberta, Canada [59] and North Dakota [86] shows little difference between burned and unburned sites, and no detectable postfire trend in field sowthistle abundance 1 to 2 years after fire.

Flowering of field sowthistle may increase after fire. Postfire flowering response may be related to postfire moisture availability [91].

Field sowthistle may establish on burned sites from wind-dispersed seed. Soil samples were taken from burned and unburned areas of a 270-year-old red pine forest in Minnesota 3 years after wildfire. No field sowthistle germinants emerged from soil taken from unburned areas, while the equivalent of 109,000 field sowthistle seedlings per hectare emerged from soil taken from burned areas. No field sowthistle plants occurred in either burned or unburned plots, and no field sowthistle seeds were found in unburned soil samples. The author concluded that field sowthistle seedlings probably developed from seeds blown into the burned areas after the fire [3].

Probability of postfire establishment from offsite seed sources may be related to season of burning. Thompson and Shay [120] conducted 3 prescribed burn treatments in 3 different seasons on the Delta Marsh in Manitoba. Field sowthistle was absent from unburned plots, but seedlings established on both summer and fall burned plots, with greatest establishment 1 month following summer burns. These seedlings persisted into the following year, resulting in increased nonseedling shoot density and biomass on summer burned plots:

Mean values (95% CI) for 3 variables of field sowthistle following burning during different seasons at the Delta Marsh, Manitoba [120]

Plot type/burn date/sample date

Control August 1979 burn, sampled September 1979 August 1979 burn, sampled August 1980 October 1979 burn, sampled August 1980 May 1980 burn, sampled August 1980
Seedling density (no./m² 0 15.5 (11.5) 0 0.4 (0.4) 0
Nonseedling shoot density (no./m² 0 --- 8 (1.7) 0 0
Biomass (g/m² 0 --- 28.2 (16.9) 0.1 (0.2) 0

Field sowthistle has a long flowering period that begins in early July and continues until plants are frosted, with peak flowering in mid to late summer [110]. Summer burns on the Delta Marsh were conducted at the time of year when the most mature sowthistle seed was likely being dispersed, while timing of fall burns corresponded to a time of year when fewer seeds were likely to be available, and spring burns occurred when no field sowthistle seed would likely be available [120]. Although there is evidence that field sowthistle seeds occur in the soil seed bank in the Delta Marsh [88] (see seed banking), it is more likely that field sowthistle seedlings detected in this study [120] established from wind-dispersed seed, given the correspondence of burn season, field sowthistle phenology, and seedling establishment.

While field sowthistle is likely to persist after fire, data are insufficient for detecting trends in its postfire abundance. Simulated "light" and "deep" burns using a propane torch in both bluejoint reedgrass and willow savanna habitats in northern Alberta found little difference in field sowthistle cover 2 growing seasons after summer burning [59]:

Mean percent cover (SE) of field sowthistle following experimental burn treatments in 2 community types in Alberta [59]

Plant community

Burn treatment
None Light Deep
Bluejoint reedgrass meadow 1 (1) 2 (1) 4 (2)
Willow savanna 10 (3) 15 (5) 15 (4)

Abundance of field sowthistle plants was highly variable on burned and unburned prairie sites in a study to evaluate the effects of prescribed burning on grassland species desired for wildlife habitat on the Tewaukon National Wildlife Refuge in southeastern North Dakota. Cover of field sowthistle was mostly the same on burned and unburned sites, but in some years was either significantly higher on or significantly lower on burned versus control plots. Data show both great variation in percent canopy cover and no clear trend of increase or decrease on burned versus control plots, 1 month or 26 months after fires in May or June [86].

In northwestern Minnesota, flowering of field sowthistle increased on some sites after prescribed fire was used as part of a prairie restoration project. Burns were conducted in spring 1973, and data on flowering response were collected during the growing season of the same year. Results were based on comparison of burned and unburned transects. Field sowthistle was recorded on 3 site types in the study area: a wet-mesic site in "badly" disturbed prairie, a wet swale site in undisturbed prairie, and a gently sloping to nearly level mesic site in undisturbed prairie. Flowering increased after prescribed fire, relative to controls, on both disturbed and undisturbed wet prairie sites, but was not different from controls in the mesic prairie site [91].

Postfire colonization potential: Field sowthistle may establish on burned sites after fire [3,120], especially when burning is conducted during the flowering period [120]. Managers should be alert to this possibility when field sowthistle occurs in the vicinity of the burn area. Additionally, flowering of field sowthistle may be stimulated by prescribed burning [91], resulting in increased seed production and further increasing the likelihood of postfire establishment.

Control of field sowthistle using prescribed fire: While no research is available examining the potential for using prescribed fire to control field sowthistle, evidence from other fire studies [59,86] suggest that it is likely to persist after fire and may increase in abundance on some sites. Given the abundance of underground buds on both vertical and horizontal roots, and on basal portions of aerial stems [51,89], it is unlikely that prescribed fire would be severe enough to substantially damage established field sowthistle plants.

If field sowthistle plants are pulled or cut and placed in a pile it is possible for viable seeds to be produced if flowers are present when the plants are cut. These plants could be burned to reduce the possibility of viable seeds being produced [110].


SPECIES: Sonchus arvensis
Field sowthistle is "good" as a livestock feed [111,129]. Sheep and cattle will eat new growth and sometimes roots [133], and pronghorns were observed utilizing field sowthistle in central Montana during the fall [24].

Field sowthistle is considered "excellent" forage for rabbits [118] and Martin and others (as reported in [133], a literature review) state field sowthistle is a minor element in the diet of some North American birds.

Field sowthistle is listed as a nonnative plant occurring in critical habitat of the threatened desert tortoise in the Mojave and Colorado deserts. It is of concern because it competes with native plants vital to the tortoises' survival [17].

Palatability/nutritional value: Although field sowthistle compares favorably with alfalfa (Medicago sativa) for nutritional value, it is not especially palatable to grazing animals. Dry field sowthistle is about 10% protein by weight [19,20]. Palatability of field sowthistle to lambs was lower compared to grasses and alfalfa, and infestations of field sowthistle in pastures and hayfields may decrease overall forage feeding value [76].

Field sowthistle has equal or higher in vitro digestible dry matter, micro- and macromineral content and crude protein and lower neutral detergent fiber compared to alfalfa [76]:

Nutritional values for field sowthistle [76]
Sample date In vitro digestible dry matter concentration
(g kg-1)
Neutral detergent fiber concentration
(g kg-1)
Crude protein concentration
(g kg-1)
15 June 1981 818 312 164
29 June 1981 660 447 132
1 June 1982 792 267 214

Herbage macromineral and micromineral concentrations for field sowthistle are given in the following tables:

Herbage macromineral concentrations in g kg-1 [76]
Sample year Ca P K Mg
1981 (mean of 2 sample dates) 16.8 3.0 26.6 6.8
1982 (single sample date) 17.3 4.8 47.9 3.6

Herbage micromineral concentrations in µg g-1 [76]
Sample year Zn Cu B Mn Al Fe
1981 (mean of 2 sample dates) 22 10 26 63 393 334
1982 (single sample date) 40 10 26 53 83 108

Cover value: Cover value of field sowthistle for several classes of wildlife for 2 western states is provided by Dittberner and Olson [32] in the following table:

State Elk Mule deer White-tailed deer Pronghorn Upland game bird Waterfowl Small nongame bird Small mammal
Utah poor poor poor fair poor poor fair
North Dakota good good fair fair

Roasted roots of field sowthistle have been used like chicory (Cichorium intybus) root as an additive or a replacement for coffee. The young, tender leaves can be eaten raw in salads or cooked [118].

Most of the latex of field sowthistle is oil and may be a potential crop for oil or hydrocarbon production [19,20]. Field sowthistle is a good source of pentacyclic triterpenes, which may become important in the pharmaceutical industry [61].

Impacts: Information concerning the impacts of field sowthistle on natural communities is absent from the literature. Research is needed to determine and document what effects field sowthistle may have on wildlands.

Control: Field sowthistle is relatively resistant to many common broadleaf herbicides compared to most annual broadleaf weeds. Consequently, the best systems for control often include a combination of cultural and chemical treatments designed to reduce competition from field sowthistle, prevent seed production, and reduce the reproductive capacity of its roots (Fryer and Makepeace, 1982, as reported in a literature review [74]).

As of this writing (2004) there is no information available on control of field sowthistle in natural areas.

Prevention: The most efficient and effective method of managing invasive species is to prevent their invasion and spread [107]. Since field sowthistle seed is so easily disseminated by wind, scouting and detection are keys to preventing plant establishment [133]. It is easier to prevent initial colonization by field sowthistle than to eliminate established populations. Seedlings are easily controlled through mechanical and chemical methods. Planting weed-free crop seed and controlling field sowthistle on field borders can prevent initial infestations in wildlands adjacent to agricultural settings [133] (See Seedling establishment/growth).

Integrated management: Components of any integrated weed management program are sustained effort, constant evaluation, and the adoption of improved strategies [106]. Factors to be addressed before a management decision is made include inventory and assessment to identify the target weed(s) and determine the size of the infestation(s); assessment of nontarget vegetation, soil types, climatic conditions, and important water resources. An evaluation of the benefits and limitations of each control method also needs to be accomplished [84].

Combinations of tillage plus cultural practices or herbicides applied regularly have controlled field sowthistle in agricultural settings [30]. No information is available on integrated control measures for field sowthistle in wildlands.

Timing of control measures may increase the effectiveness of integrated management techniques. Schimming and Messersmith [102] conducted artificial freezing experiments with field sowthistle. They determined a temperature of 1 oF (-17 oC) reduced survival of field sowthistle roots by 50% and a temperature of 4 oF (-15 oC) reduced total dry weight of emerging field sowthistle shoots by 50%. The authors speculate conditions that tend to minimize hardening, such as lack of photosynthetic material in fall after tillage or chemical treatment, stimulation of fall growth after tillage, or high nitrogen levels may increase injury caused by freezing temperatures in the field.

Physical/mechanical: Tillage generally reduces field sowthistle, but its effectiveness depends on plant growth characteristics at time of tillage [10,50,52], type of tillage being utilized [30,51], and frequency of tillage [92]. Intensive tillage is usually not appropriate in wildland settings, so it is not discussed further here.

Studies of mowing as a control method for field sowthistle show mixed results. Defoliation was less effective than burial for reducing infestations of field sowthistle in a study done in Sweden in 1967 [52], suggesting mowing is not as effective as tillage for control of field sowthistle [74]. However, Stevens [110] found defoliation an efficient method to control field sowthistle. Plants grown from root cuttings planted 3 May, had their leaves removed by hoe on 23 May when the largest leaves were about 6 inches (15 cm) long. The plants had the leaves removed again on 1 June, when leaves had again grown to about 6 inches (15 cm). After the 1 June defoliation, leaf growth was less vigorous. There was "very little" regrowth of leaves after a 1 July defoliation and none after a 19 July defoliation although weather conditions were favorable for growth. No plants appeared the next spring.

Fire: See the Fire Management Considerations section of this summary.

Biological: There appears to be limited biological agents available to help control field sowthistle. A tephritid fly from Europe that transforms the seedhead of field sowthistle into a gall has been released into Canada but has not become established [53]. Cystiphora sonchi, another fly native to Europe, was released into Canada and has become established in Alberta, Saskatchewan, Manitoba, and Nova Scotia [93]. Zollinger and Parker [133] report as many as 721 galls were formed on one plant of field sowthistle, but Lemna and Messersmith [74] state that no reduction in field sowthistle because of Cystiphora sonchi has been observed. A third fly, Liriomyza sonchi, has been authorized for release into Canada (Peschken and Derby 1988, reported in [74]).

Zollinger and Parker [133] provide a literature review of biological control efforts as of 1998.

Chemical: Auxin-type herbicides are the primary chemicals used to control field sowthistle. Field sowthistle is "moderately susceptible" to auxins such as 2,4-D, 2,4-DB, and MCPA in the seedling stage, and established stands are "moderately resistant" (Fryer and Makepeace, 1982, as reported in a literature review [74]). Growth of aerial portions can be retarded by auxin-type herbicides, and flowering can be completely suppressed if the plant is treated when growth is vigorous (Fryer and Makepeace 1982 as reported in a literature review [74]), and [77]. A more detailed discussion of chemical control of field sowthistle is provided by Lemna and Messersmith [74] and by Zollinger and Parker [133].

Cultural: Patches of field sowthistle were cut for hay or were pastured as an early control measure [111,129]. An alfalfa or alfalfa-grass mixture, regularly cut for hay, can eliminate 90% of field sowthistle in 3 years (Martin and others 1961 in [74]).

"Intensive" grazing by domestic sheep or cattle weakens field sowthistle when the animals eat new growth and sometimes roots [133]. Grazing also enhances other control practices. However, field sowthistle is classified as an "increaser" under heavy grazing because it increases as more palatable plants are preferentially grazed [70].

Sonchus arvensis: REFERENCES

1. Abbas, Hamed K.; Tanaka, T.; Duke, S. O.; Boyette, C. D. 1995. Susceptibility of various crop and weed species to AAL-toxin, a natural herbicide. Weed Technology. 9(1): 125-130. [37302]
2. Agee, James K. 1994. Fire and weather disturbances in terrestrial ecosystems of the eastern Cascades. Gen. Tech. Rep. PNW-GTR-320. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 52 p. [Hessburg, Paul F., tech. ed. Eastside forest ecosystem health assessment. Vol. 3: assessment]. [23656]
3. Ahlgren, Clifford E. 1979. Emergent seedlings on soil from burned and unburned red pine forest. Minnesota Forestry Research Notes No. 273. St. Paul, MN: University of Minnesota, College of Forestry. 4 p. [16910]
4. Arno, Stephen F. 1976. The historical role of fire on the Bitterroot National Forest. Res. Pap. INT-187. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 29 p. [15225]
5. Arno, Stephen F. 1980. Forest fire history in the Northern Rockies. Journal of Forestry. 78(8): 460-465. [11990]
6. Arno, Stephen F. 2000. Fire in western forest ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 97-120. [36984]
7. Arno, Stephen F.; Fischer, William C. 1995. Larix occidentalis--fire ecology and fire management. In: Schmidt, Wyman C.; McDonald, Kathy J., comps. Ecology and management of Larix forests: a look ahead: Proceedings of an international symposium; 1992 October 5-9; Whitefish, MT. Gen. Tech. Rep. GTR-INT-319. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 130-135. [25293]
8. Arno, Stephen F.; Gruell, George E. 1983. Fire history at the forest-grassland ecotone in southwestern Montana. Journal of Range Management. 36(3): 332-336. [342]
9. Arno, Stephen F.; Wilson, Andrew E. 1986. Dating past fires in curlleaf mountain-mahogany communities. Journal of Range Management. 39(3): 241-243. [350]
10. Arny, A. C. 1932. Variations in the organic reserves in underground parts of five perennial weeds from late April to November. Technical Bulletin 84. St. Paul, MN: University of Minnesota, Agricultural Experiment Station. 28 p. [48290]
11. Baisan, Christopher H.; Swetnam, Thomas W. 1990. Fire history on a desert mountain range: Rincon Mountain Wilderness, Arizona, U.S.A. Canadian Journal of Forest Research. 20: 1559-1569. [14986]
12. Barrett, Stephen W. 1993. Fire regimes on the Clearwater and Nez Perce National Forests north-central Idaho. Final Report: Order No. 43-0276-3-0112. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory. Unpublished report on file with: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory, Missoula, MT. 21 p. [41883]
13. Barrett, Stephen W.; Arno, Stephen F.; Key, Carl H. 1991. Fire regimes of western larch - lodgepole pine forests in Glacier National Park, Montana. Canadian Journal of Forest Research. 21: 1711-1720. [17290]
14. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434]
15. Bosy, J.; Aarssen, L. W. 1995. The effect of seed orientation on germination in a uniform environment: differential success without genetic or environmental variation. Journal of Ecology. 83(5): 769-773. [44984]
16. Braidek, J. T.; Fedec, P.; Jones, D. 1984. Field survey of halophytic plants of disturbed sites on the Canadian prairies. Canadian Journal of Plant Science. 64: 745-751. [24018]
17. Brooks, Matthew L.; Esque, Todd C. 2002. Alien plants and fire in desert tortoise (Gopherus agassizii) habitat of the Mojave and Colorado deserts. Chelonian Conservation Biology. 4(2): 330-340. [44468]
18. Bruns, V. F. 1965. The effects of fresh water storage on the germination of certain weed seeds. Weeds. 13: 38-39. [48293]
19. Buchanan, R. A.; Cull, I. M.; Otey, F. H.; Russell, C. R. 1978. Hydrocarbon- and rubber-producing crops. Economic Botany. 32: 131-145. [47819]
20. Buchanan, R. A.; Otey, F. H.; Russell, C. R.; Cull, I. M. 1978. Whole-plant oils, potential new industrial raw materials. Journal of the American Oil Chemists' Society. 55: 657-662. [47815]
21. Buchholz, Kenneth; Good, Ralph E. 1982. Density, age structure, biomass and net annual aboveground productivity of dwarfed Pinus rigida Moll. from the New Jersey Pine Barren Plains. Bulletin of the Torrey Botanical Club. 109(1): 24-34. [8639]
22. Burkhardt, Wayne J.; Tisdale, E. W. 1976. Causes of juniper invasion in southwestern Idaho. Ecology. 57: 472-484. [565]
23. Chepil, W. S. 1946. Germination of seeds. I. Longevity, periodicity of germination, and vitality of seeds in cultivated soil. Scientific Agriculture. 26: 307-346. [48281]
24. Cole, G. F. 1956. The pronghorn antelope: Its range use and food habits in central Montana with special reference to alfalfa. Technical Bulletin 516. Bozeman, MT: Montana State College, Agricultural Experiment Station. 63 p. [43976]
25. Cooper, Charles F. 1961. Pattern in ponderosa pine forests. Ecology. 42(3): 493-499. [5780]
26. Cronquist, Arthur; Holmgren, Arthur H.; Holmgren, Noel H.; Reveal, James L.; Holmgren, Patricia K. 1994. Intermountain flora: Vascular plants of the Intermountain West, U.S.A. Vol. 5: Asterales. New York: The New York Botanical Garden. 496 p. [28653]
27. D'Antonio, Carla M. 2000. Fire, plant invasions, and global changes. In: Mooney, Harold A.; Hobbs, Richard J., eds. Invasive species in a changing world. Washington, DC: Island Press: 65-93. [37679]
28. Dale, Virginia H. 1989. Wind dispersed seeds and plant recovery on the Mount St. Helens debris avalanche. Canadian Journal of Botany. 67: 1434-1441. [12670]
29. Davis, Kathleen M. 1980. Fire history of a western larch/Douglas-fir forest type in northwestern Montana. In: Stokes, Marvin A.; Dieterich, John H., tech. coords. Proceedings of the fire history workshop; 1980 October 20-24; Tucson, AZ. Gen. Tech. Rep. RM-81. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 69-74. [12813]
30. Derscheid, Lyle A.; Nash, Russell L.; Wicks, Gail A. 1961. Thistle control with cultivation, cropping and chemicals. Weeds. 9: 90-102. [48292]
31. Derscheid, Lyle A.; Schultz, Robert E. 1960. Achene development of Canada thistle and perennial sowthistle. Weeds. 8: 55-62. [48291]
32. Dittberner, Phillip L.; Olson, Michael R. 1983. The Plant Information Network (PIN) data base: Colorado, Montana, North Dakota, Utah, and Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service. 786 p. [806]
33. Dodd, J, D.; Coupland, R. T. 1966. Vegetation of saline areas in Saskatchewan. Ecology. 47(6): 958-968. [11209]
34. Dorn, Robert D. 1988. Vascular plants of Wyoming. Cheyenne, WY: Mountain West Publishing. 340 p. [6129]
35. Duchesne, Luc C.; Hawkes, Brad C. 2000. Fire in northern ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 35-51. [36982]
36. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905]
37. Fernald, M. L.; Wiegand, K. M. 1910. A summer's botanizing in eastern Maine and western New Brunswick. Rhodora. 12(138): 101-121, 133-146. [48297]
38. Finney, Mark A.; Martin, Robert E. 1989. Fire history in a Sequoia sempervirens forest at Salt Point State Park, California. Canadian Journal of Forest Research. 19: 1451-1457. [9845]
39. Floyd, M. Lisa; Romme, William H.; Hanna, David D. 2000. Fire history and vegetation pattern in Mesa Verde National Park, Colorado, USA. Ecological Applications. 10(6): 1666-1680. [37590]
40. Frissell, Sidney S., Jr. 1968. A fire chronology for Itasca State Park, Minnesota. Minnesota Forestry Research Notes No. 196. Minneapolis, MN: University of Minnesota. 2 p. [34527]
41. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; Lewis, Mont E.; Smith, Dixie R. 1977. Vegetation and environmental features of forest and range ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of Agriculture, Forest Service. 68 p. [998]
42. Gleason, Henry A.; Cronquist, Arthur. 1991. Manual of vascular plants of northeastern United States and adjacent Canada. 2nd ed. New York: New York Botanical Garden. 910 p. [20329]
43. Gottfried, Gerald J.; Swetnam, Thomas W.; Allen, Craig D.; Betancourt, Julio L.; Chung-MacCoubrey, Alice L. 1995. Pinyon-juniper woodlands. In: Finch, Deborah M.; Tainter, Joseph A., eds. Ecology, diversity, and sustainability of the Middle Rio Grande Basin. Gen. Tech. Rep. RM-GTR-268. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 95-132. [26188]
44. Grant, Martin L. 1929. The burn succession in Itasca County, Minnesota. Minneapolis, MN: University of Minnesota. 63 p. Thesis. [36527]
45. Great Plains Flora Association. 1986. Flora of the Great Plains. Lawrence, KS: University Press of Kansas. 1392 p. [1603]
46. Greenlee, Jason M.; Langenheim, Jean H. 1990. Historic fire regimes and their relation to vegetation patterns in the Monterey Bay area of California. The American Midland Naturalist. 124(2): 239-253. [15144]
47. Gruell, G. E.; Loope, L. L. 1974. Relationships among aspen, fire, and ungulate browsing in Jackson Hole, Wyoming. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 33 p. In cooperation with: U.S. Department of the Interior, National Park Service, Rocky Mountain Region. [3862]
48. Guy, Robert D.; Reid, David M.; Krouse, H. Roy. 1986. Factors affecting 13C/12C ratios of inland halophytes. II. Ecophysiological interpretations of patterns in the field. Canadian Journal of Botany. 642: 2700-2707. [48276]
49. Guyette, Richard; McGinnes, E. A., Jr. 1982. Fire history of an Ozark glade in Missouri. Transactions, Missouri Academy of Science. 16: 85-93. [5170]
50. Hakansson, Sigurd. 1969. Experiments with Sonchus arvensis L. I. Development and growth, and the response to burial and defoliation in different developmental stages. Lantbrukshogskolans Annaler. 35: 989-1030. [48284]
51. Hakansson, Sigurd. 1982. Multiplication, growth and persistence of perennial weeds. In: Holzner, W.; Numata, M., eds. Biology and ecology of weeds. The Hague: Dr. W. Junk: 123-135. [47816]
52. Hakansson, Sigurd; Wallgren, Bengt. 1972. Experiments with Sonchus arvensis L. II. Reproduction, plant development and response to mechanical disturbance. Swedish Journal of Agricultural Research. 2: 3-14. [48381]
53. Harris, P.; Shorthouse, J. D. 1996. Effectiveness of gall inducers in weed biological control. The Canadian Entomologist. 128(6): 1021-1055. [37288]
54. Heinselman, Miron L. 1970. The natural role of fire in northern conifer forests. In: The role of fire in the Intermountain West: Symposium proceedings; 1970 October 27-29; Missoula, MT. Missoula, MT: Intermountain Fire Research Council: 30-41. In cooperation with: University of Montana, School of Forestry. [15735]
55. Hendrickson, William H. 1972. Perspective on fire and ecosystems in the United States. In: Fire in the environment: Symposium proceedings; 1972 May 1-5; Denver, CO. FS-276. [Washington, DC]: U.S. Department of Agriculture, Forest Service: 29-33. In cooperation with: Fire Services of Canada, Mexico, and the United States; Members of the Fire Management Study Group; North American Forestry Commission; FAO. [17276]
56. Heyerdahl, Emily K.; Berry, Dawn; Agee, James K. 1994. Fire history database of the western United States. Final report. Interagency agreement: U.S. Environmental Protection Agency DW12934530; U.S. Department of Agriculture, Forest Service PNW-93-0300; University of Washington 61-2239. Seattle, WA: U.S. Department of Agriculture, Pacific Northwest Research Station; University of Washington, College of Forest Resources. 28 p. [+ appendices]. Unpublished report on file with: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory, Missoula, MT. [27979]
57. Hickman, James C., ed. 1993. The Jepson manual: Higher plants of California. Berkeley, CA: University of California Press. 1400 p. [21992]
58. Hitchcock, C. Leo; Cronquist, Arthur. 1973. Flora of the Pacific Northwest. Seattle, WA: University of Washington Press. 730 p. [1168]
59. Hogenbirk, John C.; Wein, Ross W. 1991. Fire and drought experiments in northern wetlands: a climate change analogue. Canadian Journal of Botany. 69: 1991-1997. [17127]
60. Hogenbirk, John C.; Wein, Ross W. 1992. Temperature effects on seedling emergence from boreal wetland soils: implications for climate change. Aquatic Botany. 42(4): 361-373. [19959]
61. Hooper, Shirley N.; Chandler, R. Frank. 1984. Herbal remedies of the maritime Indians: phytosterols and triterpenes of 67 plants. Journal of Ethnopharmacology. 10: 181-194. [48295]
62. Hulten, Eric. 1968. Flora of Alaska and neighboring territories. Stanford, CA: Stanford University Press. 1008 p. [13403]
63. Hume, L.; Archibold, O. W. 1986. The influence of a weedy habitat on the seed bank of an adjacent cultivated field. Canadian Journal of Botany. 64: 1879-1883. [27685]
64. Jones, Stanley D.; Wipff, Joseph K.; Montgomery, Paul M. 1997. Vascular plants of Texas. Austin, TX: University of Texas Press. 404 p. [28762]
65. Kartesz, John T. 1999. A synonymized checklist and atlas with biological attributes for the vascular flora of the United States, Canada, and Greenland. 1st ed. In: Kartesz, John T.; Meacham, Christopher A. Synthesis of the North American flora (Windows Version 1.0), [CD-ROM]. Chapel Hill, NC: North Carolina Botanical Garden (Producer). In cooperation with: The Nature Conservancy; U.S. Department of Agriculture, Natural Resources Conservation Service; U.S. Department of the Interior, Fish and Wildlife Service. [36715]
66. Kinch, R. C.; Termunde, Darrold. 1957. Germination of perennial sow thistle and Canada thistle at various stages of maturity. Proceedings, Association of Official Seed Analysts. 47: 165-166. [48278]
67. Komarova, T. A. 1986. Role of forest fires in germination of seed dormant in the soil. Soviet Journal of Ecology. 16(6): 311-315. [20252]
68. Kucera, Clair L. 1981. Grasslands and fire. In: Mooney, H. A.; Bonnicksen, T. M.; Christensen, N. L.; Lotan, J. E.; Reiners, W. A., tech. coords. Fire regimes and ecosystem properties: Proceedings of the conference; 1978 December 11-15; Honolulu, HI. Gen. Tech. Rep. WO-26. Washington, DC: U.S. Department of Agriculture, Forest Service: 90-111. [4389]
69. Kuchler, A. W. 1964. United States [Potential natural vegetation of the conterminous United States]. Special Publication No. 36. New York: American Geographical Society. 1:3,168,000; colored. [3455]
70. Lacey, John; Mosley, John. 2002. 250 plants for range contests in Montana. MONTGUIDE MT198402 AG 6/2002. Range E-2 (Misc.). Bozeman, MT: Montana State University, Extension Service. 4 p. [43671]
71. Lackschewitz, Klaus. 1991. Vascular plants of west-central Montana--identification guidebook. Gen. Tech. Rep. INT-227. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 648 p. [13798]
72. Larson, Gary E. 1993. Aquatic and wetland vascular plants of the Northern Great Plains. Gen. Tech. Rep. RM-238. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 681 p. Jamestown, ND: Northern Prairie Wildlife Research Center (Producer). Available: [2006, February 11]. [22534]
73. Laven, R. D.; Omi, P. N.; Wyant, J. G.; Pinkerton, A. S. 1980. Interpretation of fire scar data from a ponderosa pine ecosystem in the central Rocky Mountains, Colorado. In: Stokes, Marvin A.; Dieterich, John H., tech. coords. Proceedings of the fire history workshop; 1980 October 20-24; Tucson, AZ. Gen. Tech. Rep. RM-81. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 46-49. [7183]
74. Lemna, Wanda K.; Messersmith, Calvin G. 1990. The biology of Canadian weeds. 94. Sonchus arvensis L. Canadian Journal of Plant Science. 70: 509-532. [24019]
75. Long, Bayard. 1922. Sonchus uliginosus occurring in the Philadelphia area. Torreya. 22(6): 91-98. [48282]
76. Marten, G. C.; Sheaffer, C. C.; Wyse, D. L. 1987. Forage nutritive value and palatability of perennial weeds. Agronomy Journal. 79: 980-986. [3449]
77. May, M. J.; Smith, J. 1977. Perennial weeds and their control on organic soils. ADAS Quarterly Review. 27: 146-154. [47820]
78. McPherson, Guy R. 1995. The role of fire in the desert grasslands. In: McClaran, Mitchel P.; Van Devender, Thomas R., eds. The desert grassland. Tucson, AZ: The University of Arizona Press: 130-151. [26576]
79. Meinecke, E. P. 1929. Quaking aspen: A study in applied forest pathology. Tech. Bull. No. 155. Washington, DC: U.S. Department of Agriculture. 34 p. [26669]
80. Miller, Richard F.; Rose, Jeffery A. 1995. Historic expansion of Juniperus occidentalis (western juniper) in southeastern Oregon. The Great Basin Naturalist. 55(1): 37-45. [25666]
81. Mohlenbrock, Robert H. 1986. [Revised edition]. Guide to the vascular flora of Illinois. Carbondale, IL: Southern Illinois University Press. 507 p. [17383]
82. Moir, William H. 1982. A fire history of the High Chisos, Big Bend National Park, Texas. The Southwestern Naturalist. 27(1): 87-98. [5916]
83. Morrison, Peter H.; Swanson, Frederick J. 1990. Fire history and pattern in a Cascade Range landscape. Gen. Tech. Rep. PNW-GTR-254. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 77 p. [13074]
84. Mullin, Barbara. 1992. Meeting the invasion: integrated weed management. Western Wildlands. 18(2): 33-38. [19462]
85. Myers, Ronald L. 2000. Fire in tropical and subtropical ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 161-173. [36985]
86. Olson, Wendell W. 1975. Effects of controlled burning on grassland within the Tewaukon National Wildlife Refuge. Fargo, ND: North Dakota University of Agriculture and Applied Science. 137 p. Thesis. [15252]
87. Paysen, Timothy E.; Ansley, R. James; Brown, James K.; Gottfried, Gerald J.; Haase, Sally M.; Harrington, Michael G.; Narog, Marcia G.; Sackett, Stephen S.; Wilson, Ruth C. 2000. Fire in western shrubland, woodland, and grassland ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 121-159. [36978]
88. Pederson, Roger L. 1981. Seed bank characteristics of the Delta Marsh, Manitoba: applications for wetland management. In: Richardson, B., ed. Midwest conference on wetland values and management: Selected proceedings; 1981 June 17-19; St. Paul, MN. Minneapolis, MN: Freshwater Society: 61-69. [24016]
89. Pegtel, D. M. 1973. Aspects of ecotypic differentiation in the perennial sowthistle. Acta Horticulturae. 32: 55-71. [48287]
90. Pemadasa, M. A.; Kangatharalingam, N. 1977. Factors affecting germination of some composites. Ceylon Journal of Science (Biological Science). 12: 157-168. [48274]
91. Pemble, R. H.; Van Amburg, G. L.; Mattson, Lyle. 1981. Intraspecific variation in flowering activity following a spring burn on a northwestern Minnesota prairie. In: Stuckey, Ronald L.; Reese, Karen J., eds. The prairie peninsula--in the "shadow" of Transeau: Proceedings, 6th North American prairie conference; 1978 August 12-17; Columbus, OH. Ohio Biological Survey: Biological Notes No. 15. Columbus, OH: Ohio State University, College of Biological Sciences: 235-240. [3435]
92. Peschken, D. P. 1984. Sonchus arvensis L., perennial sow-thistle, S. oleraceus L., annual sow-thistle, and S. asper (L.) Hill, spiny annual sow-thistle (Compositae). In: Kelleher, J. S.; Hulme, M. A., eds. Biological control programmes against insects and weeds in Canada 1969-1980. Slough, UK: Commonwealth Agriculture Bureax: 205-209. [24021]
93. Peschken, D. P.; McClay, A. S.; Derby, J. L.; DeClerck, R. 1989. Cystiphora sonchi (Bremi) (Diptera: Cedidomyiidae), a new biological control agent established on the weed perennial sow-thistle (Sonchus arvensis L.) (Compositae) in Canada. The Canadian Entomologist. 121: 781-791. [24020]
94. Peschken, Diether P.; Thomas, A. Gordon; Wise, Robin F. 1983. Loss in yield of rapeseed (Brassica napus, B. campestris) caused by perennial sowthistle (Sonchus arvensis) in Saskatchewan and Manitoba. Weed Science. 31: 740-744. [48294]
95. Peters, Erin F.; Bunting, Stephen C. 1994. Fire conditions pre- and postoccurrence of annual grasses on the Snake River Plain. In: Monsen, Stephen B.; Kitchen, Stanley G., comps. Proceedings--ecology and management of annual rangelands; 1992 May 18-22; Boise, ID. Gen. Tech. Rep. INT-GTR-313. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 31-36. [24249]
96. Quinnild, Clayton L.; Cosby, Hugh E. 1958. Relicts of climax vegetation on two mesas in western North Dakota. Ecology. 39(1): 29-32. [1925]
97. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843]
98. Redmann, R. E. 1972. Plant communities and soils of an eastern North Dakota prairie. Bulletin of the Torrey Botanical Club. 99(2): 65-76. [3639]
99. Ripple, William J. 1994. Historic spatial patterns of old forests in western Oregon. Journal of Forestry. 92(11): 45-49. [33881]
100. Rowe, J. S. 1969. Lightning fires in Saskatchewan grassland. The Canadian Field-Naturalist. 83: 317-324. [6266]
101. Sapsis, David B. 1990. Ecological effects of spring and fall prescribed burning on basin big sagebrush/Idaho fescue--bluebunch wheatgrass communities. Corvallis, OR: Oregon State University. 105 p. Thesis. [16579]
102. Schimming, Wanda K.; Messersmith, Calvin G. 1988. Freezing resistance of overwintering buds of four perennial weeds. Weed Science. 36: 568-573. [24022]
103. Schultz, Brad W. 1987. Ecology of curlleaf mountain mahogany (Cercocarpus ledifolius) in western and central Nevada: population structure and dynamics. Reno, NV: University of Nevada. 111 p. Thesis. [7064]
104. Seklecki, Mariette T.; Grissino-Mayer, Henri D.; Swetnam, Thomas W. 1996. Fire history and the possible role of Apache-set fires in the Chiricahua Mountains of southeastern Arizona. In: Ffolliott, Peter F.; DeBano, Leonard F.; Baker, Malchus B., Jr.; Gottfried, Gerald J.; Solis-Garza, Gilberto; Edminster, Carleton B.; Neary, Daniel G.; Allen, Larry S.; Hamre, R. H., tech. coords. Effects of fire on Madrean Province ecosystems: a symposium proceedings; 1996 March 11-15; Tucson, AZ. Gen. Tech. Rep. RM-GTR-289. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 238-246. [28082]
105. Sheldon, J. C.; Burrows, F. M. 1973. The dispersal effectiveness of the achene-pappus units of selected Compositae in steady winds with convection. New Phytologist. 72: 665-675. [24023]
106. Sheley, Roger L.; Jacobs, James S.; Carpinelli, Michael F. 1998. Distribution, biology, and management of diffuse knapweed (Centaurea diffusa) and spotted knapweed (Centaurea maculosa). Weed Technology. 12(2): 353-362. [37449]
107. Sheley, Roger; Manoukian, Mark; Marks, Gerald. 1999. Preventing noxious weed invasion. In: Sheley, Roger L.; Petroff, Janet K., eds. Biology and management of noxious rangeland weeds. Corvallis, OR: Oregon State University Press: 69-72. [35711]
108. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United States. Denver, CO: Society for Range Management. 152 p. [23362]
109. Shumovich, W.; Montgomery, F. H. 1955. The perennial sowthistles in northeastern North America. Canadian Journal of Agricultural Science. 35: 601-605. [48280]
110. Stevens, O. A. 1924. Perennial sow thistle: Growth and reproduction. Bulletin 181. Fargo, ND: North Dakota Agricultural College, Agricultural Experiment Station. 42 p. [48289]
111. Stevens, O. A. 1926. The sow thistle. Circular 32. Fargo, ND: North Dakota Agricultural College, Agricultural Experiment Station. 16 p. [48288]
112. Stevens, O. A. 1932. The number and weight of seeds produced by weeds. American Journal of Botany. 19: 784-794. [47817]
113. Stickney, Peter F. 1989. Seral origin of species comprising secondary plant succession in Northern Rocky Mountain forests. FEIS workshop: Postfire regeneration. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. 10 p. [20090]
114. Strausbaugh, P. D.; Core, Earl L. 1977. Flora of West Virginia. 2nd ed. Morgantown, WV: Seneca Books, Inc. 1079 p. [23213]
115. Stromberg, Mark R.; Kephart, Paul; Yadon, Vern. 2001. Composition, invasibility, and diversity in coastal California grasslands. Madrono. 48(4): 236-252. [41371]
116. Stuart, John D. 1987. Fire history of an old-growth forest of Sequoia sempervirens (Taxodiaceae) forest in Humboldt Redwoods State Park, California. Madrono. 34(2): 128-141. [7277]
117. Swetnam, Thomas W.; Baisan, Christopher H.; Caprio, Anthony C.; Brown, Peter M. 1992. Fire history in a Mexican oak-pine woodland and adjacent montane conifer gallery forest in southeastern Arizona. In: Ffolliott, Peter F.; Gottfried, Gerald J.; Bennett, Duane A.; Hernandez C., Victor Manuel; Ortega-Rubio, Alfred; Hamre, R. H., tech. coords. Ecology and management of oak and associated woodlands: perspectives in the southwestern United States and northern Mexico: Proceedings; 1992 April 27-30; Sierra Vista, AZ. Gen. Tech. Rep. RM-218. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 165-173. [19759]
118. Szczawenski, A. F.; Turner, N. J. 1978. Edible garden weeds of Canada. Ottawa, ON: National Museum of Natural Science. 184 p. [48296]
119. Tande, Gerald F. 1979. Fire history and vegetation pattern of coniferous forests in Jasper National Park, Alberta. Canadian Journal of Botany. 57: 1912-1931. [18676]
120. Thompson, D. J.; Shay, Jennifer M. 1989. First-year response of a Phragmites marsh community to seasonal burning. Canadian Journal of Botany. 67: 1448-1455. [7312]
121. Titus, Jonathan H.; Moore, Scott; Arnot, Mildred; Titus, Priscilla J. 1998. Inventory of the vascular flora of the blast zone, Mount St. Helens, Washington. Madrono. 45(2): 146-161. [30322]
122. U.S. Department of Agriculture, Natural Resources Conservation Service. 2008. PLANTS Database, [Online]. Available: /. [34262]
123. van der Valk, A. G. 1981. Succession in wetlands: A Gleasonian approach. Ecology. 62(3): 688-696. [15751]
124. Vincent, Dwain W. 1992. The sagebrush/grasslands of the upper Rio Puerco area, New Mexico. Rangelands. 14(5): 268-271. [19698]
125. Voss, Edward G. 1996. Michigan flora. Part III: Dicots (Pyrolaceae--Compositae). Bulletin 61: Cranbrook Institute of Science; University of Michigan Herbarium. Ann Arbor, MI: The Regents of the University of Michigan. 622 p. [30401]
126. Wade, Dale D.; Brock, Brent L.; Brose, Patrick H.; Grace, James B.; Hoch, Greg A.; Patterson, William A., III. 2000. Fire in eastern ecosystems. In: Brown, James K.; Smith, Jane Kapler, eds. Wildland fire in ecosystems: Effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station: 53-96. [36983]
127. Weber, William A.; Wittmann, Ronald C. 1996. Colorado flora: eastern slope. 2nd ed. Niwot, CO: University Press of Colorado. 524 p. [27572]
128. Whisenant, Steven G. 1990. Postfire population dynamics of Bromus japonicus. The American Midland Naturalist. 123: 301-308. [11150]
129. Whiteman, R. 1936. Sow thistle control. Circular No. 115. Winnipeg, MB: Manitoba Department of Agriculture and Immigration. 7 p. [48275]
130. Wright, Henry A.; Bailey, Arthur W. 1982. Fire ecology: United States and southern Canada. New York: John Wiley & Sons. 501 p. [2620]
131. Young, James A.; Evans, Raymond A. 1981. Demography and fire history of a western juniper stand. Journal of Range Management. 34(6): 501-505. [2659]
132. Zollinger, Richard K.; Kells, James J. 1991. Effect of soil pH, soil water, light intensity, and temperature on perennial sowthistle (Sonchus arvensis L.). Weed Science. 39: 376-384. [24015]
133. Zollinger, Richard K.; Parker, Robert. 1999. Sowthistles. In: Sheley, Roger L.; Petroff, Janet K., eds. Biology and management of noxious rangeland weeds. Corvallis, OR: Oregon State University Press: 336-349. [35742]

FEIS Home Page