Plant Assessment Form
More Elaeagnus angustifolia resources
Elaeagnus angustifolia
Synonyms: Elaeagnus angustifolius
Common Names: Russian olive; oleaster
Evaluated on: 2/9/05
List committee review date: 11/03/2005
Re-evaluation date:
Evaluator(s)
California Invasive Plant Council
1442A Walnut St. #462, Berkeley, CA 94709
510-843-3902
edbrusati@cal-ipc.org
List committee members
Joe DiTomasoJohn Randall
Carla Bossard
General Comments
No general comments for this species
Table 2. Criteria, Section, and Overall Scores
Overall Score?
Moderate
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Alert Status?
No Alert
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Documentation?
2 out of 5
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Score | Documentation | |||
1.1 | ?Impact on abiotic ecosystem processes | B. Moderate | Other Published Material | |
1.2 | ?Impact on plant community | A. Severe | Reviewed Scientific Publication | |
1.3 | ?Impact on higher trophic levels | B. Moderate | Reviewed Scientific Publication | |
1.4 | ?Impact on genetic integrity | D. None | Reviewed Scientific Publication | |
2.1 | ?Role of anthropogenic and natural disturbance in establishment | A. Severe | Reviewed Scientific Publication | |
2.2 | ?Local rate of spread with no management | A. Increases rapidly | Reviewed Scientific Publication | |
2.3 | ?Recent trend in total area infested within state | B. Increasing less rapidly | ||
2.4 |
?Innate reproductive potential (see Worksheet A) |
A. High | ||
2.5 | ?Potential for human-caused dispersal | A. High | ||
2.6 | ? Potential for natural long-distance dispersal | A. Frequent | ||
2.7 | ?Other regions invaded | C. Already invaded | ||
3.1 |
?Ecological amplitude/Range (see Worksheet C) |
A. Widespread | ||
3.2 |
?Distribution/Peak frequency (see Worksheet C) |
D. Very low | Reviewed Scientific Publication |
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 Other Published Material |
Identify ecosystem processes impacted: Alters nutrient cycling and system hydrology by spreading througout woodland, connecting lowland riparian forests with more open, upland areas. High rate of evapotranspiration increases water loss compared to native trees. Eventually changes riparian sites into dry uplands. Dense thickets of Russian olive can increase fuel loads for wildfire (1). Sources of information: 1. Tu, M. 2003. Element Stewardship Abstract: Eleagnus angustifola. The Nature Conservancy, Arlington, VA. Accessed online: http://tncweeds.ucdavis.edu |
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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: Forms dense monocultures. Shades out cottonwood seedlings. Over time, will replace tall cottonwood trees with shorter olive trees. Can establish over a wider range of sites than cottonwood (1). Alters the course of plant succession (2). Sources of information: 1. Shafroth, P. B., G. T. Auble, and M. L. Scott. 1995. Germination and establishment of the native plains cottonwood (Populus deltoides Marshall subsp. monilifera) and the exotic Russian-olive (Elaeagnus angustifolia L.) Conservation Biology. 9:1169-1175 |
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Question 1.3 Impact on higher trophic levels? | B Reviewed Scientific Publication |
Identify type of impact or alteration: Has both positive and negative impacts on wildlife. Provides food and cover for some species (1, 2). In the Rocky Mountains, some riparian birds occurred frequently in monotypic Russian olive stands, but species that are obligate residents of lowland riparian tracts (northern flicker, house wren, cedar waxwing, warbling vireo, black-headed grosbeak) were absent from Russian olive stands (2). Russian olive stands supported avian communities intermediate in species richness and alpha diversity to native riparian and upslope areas (2). Sources of information: 1. Olson, T. E., and F. L. Knopf. 1986. Naturalization of Russian-olive in the western United States. Western Journal of Applied Forestry. 1: 65-69 |
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Question 1.4 Impact on genetic integrity? | D Reviewed Scientific Publication |
none No native Eleagnus in California. Sources of information: Hickman, J. C. (ed.) 1993. The Jepson Manual, Higher Plants of California. University of California Press. Berkeley, CA enter text here |
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Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
A Reviewed Scientific Publication |
Describe role of disturbance: Does not appear to require disturbance to establish because seeds can germinate on undisturbed soils. Sources of information: 1. Lesica and Miles 1999 |
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Question 2.2 Local rate of spread with no management? | A Reviewed Scientific Publication |
Describe rate of spread: Can spread rapidly. Sources of information: 1. Olson and Knopf. 1986. |
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Question 2.3 Recent trend in total area infested within state? | B |
Describe trend: Not spreading as fast as in southwestern states. Sources of information: John Randall, The Nature Conservancy, Invasive Species Initiative, pers. obs. |
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Question 2.4 Innate reproductive potential? | A |
Describe key reproductive characteristics: Long-lived tree. Bears fruit at three to five years. Seeds can germinate anytime between fall and spring, and remain viable for up to three years. Can reproduce sexually or vegetatively. Seedlings are shade-tolerant. Numerous root suckers are produced at the root crown after disturbance or damage to aboveground tree from fire, cutting, or girdling (1). Sources of information: 1. Tu 2003 |
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Question 2.5 Potential for human-caused dispersal? | A |
Identify dispersal mechanisms: Planted as a windbreak tree and for wildlife enhancement (1), as well as for erosion control and highway beautification (2). Found in Cal-IPC nursery survey 2004. Sources of information: 1. Lesica, P., and S. Miles. 1999 Russian olive invasion into cottonwood forests along a regulated river in north-central Montana. Canadian Journal of Botany. 77:1077-1083. |
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Question 2.6 Potential for natural long-distance dispersal? | A |
Identify dispersal mechanisms: Fruits dispersed by birds (1), but transport by water is probably more important because this is a riparian species (2). Sources of information: 1. Lesica and Miles 1999 |
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Question 2.7 Other regions invaded? | C |
Identify other regions: Naturalized in riparian areas throughout the U.S (1), primarily in western states (2). Can invade both upland and riparian bottomlands (3). Sources of information: 1. Lesica and Miles 1999 |
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Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | A |
Present in Inyo, Tulare, and San Diego Counties (1). Riparian areas, flood plains, grasslands, roadsides, fencerows, seasonally moist pastures, ditches, and other disturbed sites. Often inhabits seasonally moist areas and sites near farmlands. Grows under a wide range of environmental conditions, including clay, sandy, and fairly alkaline or saline soils. Grows best in inland areas with warm summers and cold winters. Tolerates drought, high water tables, and temperatures well below freezing (to -45 degrees C or -50 degrees F) to as high as 46 degrees C (115 degrees F). San Joaquin Valley, San Francisco Bay region, eastern Sierra Nevada, Mojave Desert, mostly to 1500 m. Western states, central states, most northeastern and eastern states, a few southern states (2). Sources of information: 1. USDA, NRCS. 2004. The PLANTS Database, Version 3.5 (http://plants.usda.gov). National Plant Data Center, Baton Rouge, LA 70874-4490 USA |
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Question 3.2 Distribution/Peak frequency? | D Reviewed Scientific Publication |
Describe distribution: Sources of information: |
Worksheet A - Innate reproductive potential
Reaches reproductive maturity in 2 years or less | No |
Dense infestations produce >1,000 viable seed per square meter | No |
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 | Yes |
Has quickly spreading vegetative structures (rhizomes, roots, etc.) that may root at nodes | Yes |
Fragments easily and fragments can become established elsewhere | No |
Resprouts readily when cut, grazed, or burned | Yes |
Total points: | 6 |
Total unknowns: | 0 |
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 | ||
chenopod scrub | ||
montane dwarf scrub | ||
Upper Sonoran subshrub scrub | ||
chaparral | ||
Grasslands, Vernal Pools, Meadows, and other Herb Communities | coastal prairie | |
valley and foothill grassland | ||
Great Basin grassland | D, < 5% | |
vernal pool | ||
meadow and seep | D, < 5% | |
alkali playa | D, < 5% | |
pebble plain | ||
Bog and Marsh | bog and fen | |
marsh and swamp | ||
Riparian and Bottomland habitat | riparian forest | |
riparian woodland | ||
riparian scrub (incl.desert washes) | D, < 5% | |
Woodland | cismontane woodland | |
piñon and juniper woodland | ||
Sonoran thorn woodland | ||
Forest | broadleaved upland forest | |
North Coast coniferous forest | ||
closed cone coniferous forest | ||
lower montane coniferous forest | ||
upper montane coniferous forest | ||
subalpine coniferous forest | ||
Alpine Habitats | alpine boulder and rock field | |
alpine dwarf scrub | ||
Amplitude (breadth): | B | |
Distribution (highest score): | D |
Infested Jepson Regions
Click here for a map of Jepson regions
- Central West
- Great Valley
- Northwest
- Sierra Nevada
- Southwest
- Modoc Plateau
- Sierra Nevada East
- Desert Province
- Mojave Desert
- Sonoran Desert