Plant Assessment Form
More Centaurea stoebe ssp. micranthos resources
Centaurea stoebe ssp. micranthos
Synonyms: Centaurea maculosa; Centaurea biebersteinii, Centaurea stoebe ssp. stoebe and ssp. maculosa; Centaurea stoebe subsp. australis
Common Names: spotted knapweed
Evaluated on: 1/21/05
List committee review date: 08/07/2005
Re-evaluation date:
Evaluator(s)
Cal-IPC
530-400-8992
gmskurka@cal-ipc.org
University of California-Davis
Dept. Plant Sci., Mail Stop 4, Davis, CA 95616
530-754-8715
jmditomaso@ucdavis.edu
List committee members
Carla BossardJohn Randall
Carri Pirosko
Dan Gluesenkamp
Gina Skurka
Brianna Richardson
General Comments
Removed second scientific name, Centaurea maculosa, and added it to the synonym line 3/28/17. Ramona Robison
Table 2. Criteria, Section, and Overall Scores
Overall Score?
High
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Alert Status?
No Alert
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Documentation?
3.5 out of 5
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Score | Documentation | |||
1.1 | ?Impact on abiotic ecosystem processes | B. Moderate | Reviewed Scientific Publication | |
1.2 | ?Impact on plant community | A. Severe | Reviewed Scientific Publication | |
1.3 | ?Impact on higher trophic levels | A. Severe | Reviewed Scientific Publication | |
1.4 | ?Impact on genetic integrity | D. None | Other Published Material | |
2.1 | ?Role of anthropogenic and natural disturbance in establishment | B. Moderate | Reviewed Scientific Publication | |
2.2 | ?Local rate of spread with no management | A. Increases rapidly | Other Published Material | |
2.3 | ?Recent trend in total area infested within state | B. Increasing less rapidly | Observational | |
2.4 |
?Innate reproductive potential (see Worksheet A) |
A. High | Reviewed Scientific Publication | |
2.5 | ?Potential for human-caused dispersal | B. Moderate | Reviewed Scientific Publication | |
2.6 | ? Potential for natural long-distance dispersal | B. Occasional | Reviewed Scientific Publication | |
2.7 | ?Other regions invaded | B. Invades 1 or 2 ecological types | Other Published Material | |
3.1 |
?Ecological amplitude/Range (see Worksheet C) |
A. Widespread | Other Published Material | |
3.2 |
?Distribution/Peak frequency (see Worksheet C) |
D. Very low | Observational |
Table 3. Documentation
Scores are explained in the "Criteria for Categorizing Invasive Non-Native Plants that Threaten Wildlands".
Section 1: Impact | |
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Question 1.1 Impact on abiotic ecosystem processes? | B Reviewed Scientific Publication |
Identify ecosystem processes impacted: Stout elongated taproot may decrease soil moisture. Knapweed infestation can increase surface run-off and sedimentation. They are poor protectors of soil and water resources and they pose a wildfire threat. Success could be attributed to greater use, or more efficient use, of available soil nitrogen. Soil N often limits growth on semi-arid grasslands. Greater or more efficient use of soil N by spotted knapweed may inhibit establishment, survival, or reproduction of native grassess, if this occurred, but it doesn't. Also, Centaurea's success as an invasive species in North america cannot be attributed to greater use of soil water or greater water-use efficiency than native grasses. Knapweed infestation on bunchgrass rangeland is detrimental to water and soil resources. Lacy 1989 determined that surface water runoff and stream sediment yield were 56 and 192% higher, respectively, for spotted knapweed-dominated sites compared to bunchgrass-dominated sites. Bareground and water infiltration rates were greater on sites with unclipped bunchgrass than on those with spotted knapweed. Moderate alteration of ecosystem processes by decreasing soil moisture and facilitating erosion. Sources of information: Hoffman, Kerns. Wisconsin Manual of Control Recommendations for Ecologically Invasive Plants. Pgs 44-47. 1997. |
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Question 1.2 Impact on plant community composition, structure, and interactions? |
A Reviewed Scientific Publication |
Identify type of impact or alteration: Spotted knapweed often attains high densities on sunny wild lands, even those undisturbed by human or livestock activitiy. Knapweed thends to dominate sites at the expense of community diversity or forage production. C. maculosa reduces the productivity of desirable forage plants and floristic diversity. It has the ability to invade mature native bunchgrass communities. Decreased bluebunch wheatgrass yield was correlated with increased production of spotted knapweed. Bluebunch wheatgrass-rough fescue production was reduced by 88% by knapweed invasion. Moderate alteration of plant community composition by reduction in survivorship of native grasses Sources of information: Hoffman, Kerns. Wisconsin Manual of Control Recommendations for Ecologically Invasive PLants. Pgs. 44-47. 1997. |
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Question 1.3 Impact on higher trophic levels? | A Reviewed Scientific Publication |
Identify type of impact or alteration: Knapweeds are grazed by dear and sheep. These plants also provide nectar and pollen for domestic bees. Domestic animals and wildlife such as elk rely on range grasses and herbs for up to 80% of diet. Knapweed encroachment can destroy the forage base and would result in a significant decline in deer and elk numbers. Detrimental to range resource values because they have low platability to livestock and wildlife. Spotted knapweed reduces livestock forage and negatively impacts wildlife. Elk use was reduced by 98% on spotted knapweed-dominated range compared to bunchgrass-dominated sites. Spoon 1983 predicted a loss of 220 elk annually in Montana because of spotted knapweed infestations on winter range. Sources of information: Knapweed: Its Cost to British Columbia. Pamphlet from Province of British Columbia, Ministry of Agriculture, Fisheries and Food. |
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Question 1.4 Impact on genetic integrity? | D Other Published Material |
none No native Centaurea species in California. Sources of information: Hickman, J. (ed.) 1993. The Jepson Manual, Higher Plants of California. University of California Press. Berkeley, CA. |
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Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
A Other Published Material |
Describe role of disturbance: Spotted knapweed has invaded relatively undisturbed native plant communities and natural areas as well as heavily disturbed sites. Moderate invasive potential - this species may occasionally establish in undistrubed areas but can readily establish in areas with natural disturbances. Sources of information: Hoffman, Kerns. Wisconsin Manual of Control Recommendations for Ecologically Invasive Plants. Pgs 44-47. 1997. |
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Question 2.2 Local rate of spread with no management? | A Other Published Material |
Describe rate of spread: Has spread rapidly in most other western states. Sources of information: Duncan, C.L. and J.K. Clark (eds.). 2005. Invasive plants of range and wildlands and their environmental, ecological, and societal impacts. WSSA. |
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Question 2.3 Recent trend in total area infested within state? | B Observational |
Describe trend: Through the efforts of CDFA, spotted knapweed populations have remained about stable over the past few years. Without these efforts it is very likely that the infestations would expand exponentially, as they have in so many other states. Sources of information: DiTomaso, observational. |
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Question 2.4 Innate reproductive potential? | A Reviewed Scientific Publication |
Describe key reproductive characteristics: Reproduces solely by seed. Individual flower heads bloom from late June through August for 2-6 days each. The bracts reopen after about 20 days and scatter seeds. Plants average about 1,000 seeds per plant. Seeds are viable for seven years, and germinate throughout the growing season. Seed production was 1,000-fold that needed to maintain observed levels of infestation. Lives up to 9 years and is able to produce seeds each year. Seed production of spotted knapweed ranges from 5,000 to 40,000 seeds/m2, with more seeds produced during wet years. High. 7 points Sources of information: Hoffman, Kerns. Wisconsin Manual of Control Recommendations for Ecologically Invasive Plants. Pgs 44-47. 1997. |
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Question 2.5 Potential for human-caused dispersal? | B Reviewed Scientific Publication |
Identify dispersal mechanisms: People spread knapweed as it is easily caught up and transported great distances in the undercarriage and doors of recreational vehicles, trains, light aircraft landing at infested air strips, logging trucks and heavy machinery. It is also spread by florists who use knapweed in dried floral arrangements, movement of hay from knapweed infested to non-infested areas. Spotted knapweed flower heads also become attached to the undercarriages of vehicles, are transported long distances in mud, and commonly become attached to or drop into shoes. May also be transported in wood brought from Washington for log cabin kits. There are numerous opportunities for dispersal to new areas, but not as high as some other species. Sources of information: Knapweed: Its Cost to British Columbia. Pamphlet from Province of British Columbia, Ministry of Agriculture, Fisheries and Food. |
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Question 2.6 Potential for natural long-distance dispersal? | B Reviewed Scientific Publication |
Identify dispersal mechanisms: Spread by cattle, deer, and elk may pick up the weed and disperse it, and some bird species and small rodents eat knapweed seed. Soil disturbance provides an ideal seedbed for new knapweed infestation. Spotted knapweed plants do not break off at ground level, and populations are largely extended through peripheral enlargement of existing stands. Movement of stem by wind or passing animals can flick the loosely held achenes up to 1 m from the parent plant. Long distance transport occurs when achenes become attached to passing animals, or by rodents and birds. Long-distnace dispersal by animals or abiotic mechanisms can occur but is not the primarily means of dispersal. Sources of information: Knapweed: Its Cost to British Columbia. Pamphlet from Province of British Columbia, Ministry of Agriculture, Fisheries and Food. |
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Question 2.7 Other regions invaded? | B Other Published Material |
Identify other regions: This plant was probably introduced in the late 1890s as a contaminant in alfalfa or hay seed from Europe and Asia. Spotted knapweed, a native of Europe, was collected on Vancouver Island, British Columbia, in 1905 and San Juan Island, Washington, in 1923. By the 1930s it was common in Montana and northern Idaho. Sources of information: Duncan, C.L. and J.K. Clark (eds.). 2005. Invasive plants of range and wildlands and their environmental, ecological, and societal impacts. WSSA. |
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Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | A Other Published Material |
Can occur in Great Basin grasslands, foothill prairie, riparian habitats, along gravel bars. Habitats based on review committee observations. Sources of information: Duncan, C.L. and J.K. Clark (eds.). 2005. Invasive plants of range and wildlands and their environmental, ecological, and societal impacts. Weed Science Society of America. |
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Question 3.2 Distribution/Peak frequency? | D Observational |
Describe distribution: Not commonly encountered because of the efforts of CDFA Sources of information: DiTomaso, observational. |
Worksheet A - Innate reproductive potential
Reaches reproductive maturity in 2 years or less | Yes |
Dense infestations produce >1,000 viable seed per square meter | Yes |
Populations of this species produce seeds every year. | Yes |
Seed production sustained over 3 or more months within a population annually | No |
Seeds remain viable in soil for three or more years | Yes |
Viable seed produced with both self-pollination and cross-pollination | Unknown |
Has quickly spreading vegetative structures (rhizomes, roots, etc.) that may root at nodes | No |
Fragments easily and fragments can become established elsewhere | No |
Resprouts readily when cut, grazed, or burned | Yes |
Total points: | 7 |
Total unknowns: | 1 |
Total score: | A? |
Related traits:
Worksheet B - Arizona Ecological Types is not included here
Worksheet C - California Ecological Types
(sensu Holland 1986)Major Ecological Types | Minor Ecological Types | Code? |
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Marine Systems | marine systems | |
Freshwater and Estuarine | lakes, ponds, reservoirs | |
Aquatic Systems | rivers, streams, canals | |
estuaries | ||
Dunes | coastal | |
desert | ||
interior | ||
Scrub and Chaparral | coastal bluff scrub | |
coastal scrub | ||
Sonoran desert scrub | ||
Mojavean desert scrub (incl. Joshua tree woodland) | ||
Great Basin scrub | D, < 5% | |
chenopod scrub | ||
montane dwarf scrub | ||
Upper Sonoran subshrub scrub | ||
chaparral | ||
Grasslands, Vernal Pools, Meadows, and other Herb Communities | coastal prairie | |
valley and foothill grassland | D, < 5% | |
Great Basin grassland | D, < 5% | |
vernal pool | ||
meadow and seep | D, < 5% | |
alkali playa | ||
pebble plain | ||
Bog and Marsh | bog and fen | |
marsh and swamp | ||
Riparian and Bottomland habitat | riparian forest | D, < 5% |
riparian woodland | ||
riparian scrub (incl.desert washes) | ||
Woodland | cismontane woodland | D, < 5% |
piñon and juniper woodland | ||
Sonoran thorn woodland | ||
Forest | broadleaved upland forest | |
North Coast coniferous forest | ||
closed cone coniferous forest | ||
lower montane coniferous forest | D, < 5% | |
upper montane coniferous forest | ||
subalpine coniferous forest | ||
Alpine Habitats | alpine boulder and rock field | |
alpine dwarf scrub | ||
Amplitude (breadth): | A | |
Distribution (highest score): | D |
Infested Jepson Regions
Click here for a map of Jepson regions
- CA Floristic Province
- Cascade Range
- Central West
- Great Valley
- Northwest
- Sierra Nevada
- Southwest
- Great Basin Province
- Modoc Plateau
- Sierra Nevada East
- Desert Province
- Mojave Desert