This description provides characteristics that may be relevant to fire ecology, and is not meant for identification. It is based on descriptions from syntheses, literature reviews ([16,49,96,172]), and florae ([46,74,86,94,115,161,196,198]). Keys for identification are available (e.g. [46,74,87,94,98,198]). Russian-olive can resemble some willow species with light green foliage, particularly sandbar willow. However, unlike Russian-olive, willows have inconspicuous flowers on erect stalks and small, wind-dispersed seeds [52]. It is important to be certain of identification before control measures are begun. In the eastern United States, Russian-olive may be confused with another nonnative invasive tree, autumn-olive (Elaeagnus umbellata). Mehrhoff and others [119] provide a descriptive comparison to distinguish these species.
Russian-olive is a perennial, tree or large multi-stemmed shrub. It has dark, smooth and sometimes shredding bark. Its branches are flexible and often armed with coarse thorns. Russian-olive is described as between 16 and 40 feet (5-12 m) tall, with trunks 4 to 20 inches (10-50 cm) thick. Borell [16] describes unpruned Russian-olive trees with 5 to 6 main stems starting near the ground and growing 12 to 20 feet (4-6 m). He suggests that if pruned to 1 stem, Russian-olive on good soil with plenty of water can grow to 40 feet (12 m) tall [16]. Field observations of naturalized Russian-olive in Montana indicate that it frequently branches at ground level, about 4 to 8 inches (10-20 cm) above the root crown in moist, unshaded sites; and branches further above ground level in drier, shaded habitats [112].
Russian-olive is deciduous, with alternate, petiolate leaves in small lateral clusters on twigs of the current year. Shape and vesture of Russian-olive leaves varies among individuals and within the canopy of single trees [102,196]. Descriptions of Russian-olive leaf size range from 0.8 to 4 inches (2-10 cm) long and 0.4 to 1.6 inches (1-4 cm) wide, and leaf shape is generally described as lanceolate to oblong and sometimes elliptic. Russian-olive produces fragrant flowers, 3-12 mm long, in small axillary clusters on the twigs of the current year. Fruits are drupe- or berry-like, oval-shaped, 0.4 to 0.8 inch (1-2 cm) long. A single, relatively large, 6-13 mm, oblong achene is enclosed in the fleshy fruit.
Roots: There are few descriptions of Russian-olive's root system in the literature. It is generally described as extensive [172] or deep, with many well-developed laterals. In deep soil with a calcareous clayey subsoil and water table below 15 feet (5 m), a 25-year-old, 26-foot-tall (8 m) Russian-olive had roots as long as 39 feet (12 m). A measure of root distribution by depth indicated that 23.4% of roots were in the 1st foot of soil, 26.5% in the 2nd foot, 31.6% in the 3rd foot, 18.3% in the 4th foot, and roots were rare below 4 feet (1.2 m) [203].
Depending on location and site conditions, Russian-olive roots sometimes associate with nitrogen-fixing bacteria (Frankia spp.)[117,149,179,206]. Cross-inoculation assays of Frankia isolates indicate that Frankia strains that infect Russian-olive may also infect plant species in the Rhamnaceae and Betulaceae families [17,40]. Because Russian-olive has been a common nursery plant, the scientific literature is rich with information on Frankia symbiosis and nitrogen fixation in Russian-olive, but this topic is beyond the scope of this review.
Growth habit/stand structure: Russian-olive's growth habits (e.g. stem and foliage density, canopy cover) seem to vary between plant communities in which it occurs, and depend on size and age of associated species, as well as history of disturbance of the site. In many sites Russian-olive grows in dense thickets with close spacing [16,47,59,81,140,168], sometimes with scattered mature cottonwood in the canopy [128]. On some southwestern riparian sites, dense, nearly monotypic stands of tamarisk and/or Russian-olive form a nearly continuous, closed canopy with no distinct overstory layer. Canopy height generally averages 16 to 33 feet (5-10 m), with canopy density uniformly high. The lower 6.5 feet (2 m) of vegetation often contains a tangle of dense, often dead, branches. Live foliage density may be relatively low from 0 to 6.5 feet (2 m) above ground, but increases higher in the canopy ([188] and references therein). Russian-olive may also grow as scattered individuals or groups under a canopy of mature riparian vegetation (e.g., [47,100,128,168]) or in mixed stands of varying canopy height and density (e.g., [100,128]).
Katz and Shafroth [96] present the following table describing density and cover of several established Russian-olive populations in western North America:
River or Location Density (plants/ha) Cover (%) Source Rio Grande, NM 52-357ª N/A Freehling 1982 Rio Grande, NM 0-566b 0-43.3 Hink and Ohmart 1984 Rio Grande, NM N/A 11.1-34.8 [91] Chinle Wash, AZ 430-1150c 25-78 [20] Duchesne R., UT N/A 50 Milliken, CO N/A 40 [103] Arikaree R., CO 0.7-225.2 N/A S. Fk. Republican R., CO 4.3-314.3 N/A [97] Platte R., NE N/A 2.2-24.5 [47] Marias R., MT 20-760 (avg. 186) N/A Yellowstone R., MT 20-5,120 (avg. 676) N/A [112] Snake R., ID N/A 80 [103] Snake R., ID 940 81.2 [25] Snake R., ID 0-55 N/A [55] a Only individuals >8cm diameter at breast height and >2 m tall sampled
Russian-olive is native to southern Europe and to central and western Asia [114,142]. Within this region it occurs primarily on coasts, in riparian areas, and in other relatively moist habitats. It is also a component of several forest types, including mixed tamarisk-olive (Tamarix-Elaeagnus) forests, Russian-olive-dominated stands, cottonwood (Populus spp.)-Russian olive woodlands, and Haloxylon woodlands ([96] and references therein).
It is unclear when Russian-olive was initially introduced to North America, although its introduction as a horticultural plant was certainly intentional. Russian-olive has been cultivated for shade, hedges, wind- and snowbreaks, soil stabilization, wildlife habitat, landscaping, and to provide pollen for honeybees both in its native range and in North America [16,94,96,198]. It was introduced to many of the Great Plains and southwestern states by the early 1900s, and remained a cultivated landscape plant for many decades [41,177]. It was used extensively in windbreaks throughout the Great Plains in the 1930s and 1940s in association with government programs. As recently as the 1980s and 1990s, some state and federal agencies continued to subsidize distribution of Russian-olive seedlings in the U.S. and Canada [96,137].
Russian-olive became prominent outside cultivated areas in the western U.S. about 2 to 5 decades after it was introduced [41]. Most recommendations for planting are from the early 1900s, and escapes (or naturalization) are reported from the 1930s through 60s in Nevada, Arizona, New Mexico, Colorado, Idaho, Texas, and California ([41,67] and references therein).
Russian-olive now occurs throughout most of the U.S. including all western states but excluding most southeastern states. Plants database provides a state distribution map of Russian-olive. It is most problematic in the Southwest, Intermountain West, and Great Plains regions of the U.S. [52]. Olson and Knopf [138] give detailed Russian-olive distribution information for 17 western states as of 1986. While it is present in much of the central and northeastern U.S., it is generally described as only occasionally or rarely escaping cultivation ([96] and references therein). In Canada, Russian-olive occurs in all of the southern mainland provinces except Saskatchewan and Newfoundland [93]. It is reported to be spreading from cultivation in British Columbia, Alberta, Manitoba, and southern Ontario. Russian-olive was not considered a species of concern in Canada in 1996 (based on a national survey) [78]. There are no documented occurrences of Russian-olive in Mexico; however, suitable sites may exist in parts of the Sierra Madre of Chihuahua and Sonora ([96] and references therein). Russian-olive has also spread from cultivation in semiarid parts of South America [102].
The following lists include vegetation types in which Russian-olive is known or thought to be potentially invasive, based on reported occurrence and biological tolerances to site conditions. Because Russian-olive is most invasive in riparian areas in the western U.S., some upland habitats bordering vulnerable riparian areas are also included. Precise distribution information is limited in some areas, particularly in eastern North America; therefore, these lists may not be exhaustive.
Fire adaptations: There is no information in the literature specifically addressing fire adaptations in Russian-olive. Several workers report that Russian-olive sprouts from the trunk, root crown, and/or roots after top-kill or damage [34,49,52,59,112,140,148,172], and some report sprouting from roots and root crown following fire [35,201].
The hard-coated seed of Russian-olive may require scarification for germination (see Germination), suggesting the possibility of fire scarification. However, this has not been reported in the literature.
The growth habit (i.e. fuel arrangement) of Russian-olive varies among plant communities in which it occurs, depending on site characteristics, size and age of Russian-olive and associated species. Russian-olive stands are sometimes dense thickets of varying size, with scattered mature cottonwood in the canopy [128]. Sometimes stands are so dense that other riparian species are excluded entirely [47,59,81,128,140,168]. On some sites, especially where absence of flooding contributes to Russian-olive invasion, Russian-olive forms a sprawling to dense subcanopy under an overstory canopy of cottonwood [47,128,168]. In some cases, dense growth of Russian-olive may be more fire-prone than native communities that it invades, although this has not been studied or reported in the literature (Also see Growth habit/stand structure).
FIRE REGIMES: Information on FIRE REGIMES in which Russian-olive evolved is lacking. Similarly, there is little quantitative information on prehistoric frequency, seasonality, severity and spatial extent of fire in North American riparian ecosystems, where Russian-olive is commonly invasive. Fire frequency in these ecosystems probably varied with drought cycles, prevalence of lightning strikes, prevalence of burning by Native Americans, and frequency of fires in surrounding uplands. Fire was probably more frequent along rivers in grassland and savanna biomes than in deserts, chaparral shrublands, and conifer forests (see Fire Regime table, below) [188].
Fires in low- to mid-elevation southwestern riparian plant communities dominated by cottonwood, willow and/or mesquite (Prosopis spp.) are thought to have been infrequent [29]. Evidence used to support this supposition includes the high water content of most riparian forests; low fire frequency in much of the surrounding uplands (Sonoran and Mojave deserts, and drier portions of Chihuahuan Desert and Great Basin desert scrub); and suggestions that the dominant trees in these communities, notably Fremont and Rio Grande cottonwood, are not well-adapted to fire [28,61,188]. There remains, however, considerable uncertainty as to the effects of fire on cottonwood [60], with limited and mixed experimental evidence (e.g. [1,13,60,173]). The role of fire in these ecosystems as a whole is not well understood [60,174].
Increases in fire size or frequency have been reported in riparian areas along some southwestern [27,173,174,181] and California [23] rivers in recent decades [188]. These increases are attributed to a number of factors including an increase in ignition sources [23,174,181], increased fire frequency in surrounding uplands (e.g., [22]), increased abundance of fuels [29,60,61,135], and changes in fuel characteristics brought about by invasion of nonnative plant species (also see tamarisk in FEIS).
Several interrelated factors have contributed to increased fuel loads and changes in fuel characteristics in many riparian communities. Disturbance regimes in many southwestern riparian communities have been altered by factors including dams and diversions, groundwater pumping, agriculture, and urban development, all of which have contributed to reduced base flows, lowered water tables, less frequent inundation, and changes in the frequency, timing and severity of flooding [5,64]. The result is a drier floodplain environment where much of the native broad-leaved vegetation becomes senescent or dies, and is replaced by more drought-tolerant vegetation such as tamarisk [5,64,160] and Russian-olive [33,156]. Natural flood regimes that once served to clear away live and dead vegetation and redistribute it in a patchy nature on the floodplain are suppressed, leading to increased build-up and continuity of fuels [29,60,61,135]. Typical stand conditions on the Middle Rio Grande, for example, are now characterized by mature and over-mature Rio Grande cottonwood trees, with accumulations of dead wood and litter on the forest floor [174]. The organic matter that has accumulated on the floor of riparian forests along the middle Rio Grande now averages over 50,000 kg/ha in some areas [123].
The structure of stands supporting nonnative invasive species may carry fire better than that of native vegetation. Saltcedar and Russian-olive can contribute to increased vertical canopy density, creating volatile fuel ladders, thereby increasing the likelihood and impacts of wildfire [174]. The spread of highly flammable, nonnative vegetation such as tamarisk, giant reed (Arundo donax), red brome (Bromus madritensis), and cheatgrass in these communities, "is due partly to the same changes in flow regimes that render riparian areas more flammable, making it difficult to disentangle the effects of the nonnative species from the effects of the management factors that have enhanced their spread" [188].
In summary, the likelihood of fire in southwestern riparian ecosystems is greatest with the combination of flood suppression, water stress, and presence of nonnative species. Additionally, in the absence of flooding, regeneration of native trees is impeded and organic matter accumulates, thus increasing chances for future fires that may further alter the species composition and structure of southwestern riparian forests and promote the spread of fire-tolerant nonnative species [60,61]. Fires have replaced floods as the primary disturbance factor in many southwestern riparian ecosystems. With its ability to sprout following top-kill, and more persistent seed bank, Russian-olive may be better adapted to persist in an environment of frequent fires than native riparian trees. More research is needed to understand Russian-olive's response to fire and its ability to establish and/or persist in the postfire environment.
The following list provides fire return intervals for plant communities and ecosystems where Russian-olive may be important. It may not be all-inclusive. 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) maple-beech-birch Acer-Fagus-Betula > 1,000 silver maple-American elm Acer saccharinum-Ulmus americana < 35 to 200 [195] bluestem prairie Andropogon gerardii var. gerardii-Schizachyrium scoparium 104,139] silver sagebrush steppe Artemisia cana 5-45 [85,145,202] sagebrush steppe A. tridentata/Pseudoroegneria spicata 20-70 [139] basin big sagebrush A. tridentata var. tridentata 12-43 [154] mountain big sagebrush A. tridentata var. vaseyana 15-40 [8,26,121] Wyoming big sagebrush A. tridentata var. wyomingensis 10-70 (40**) [190,205] coastal sagebrush A. californica < 35 to < 100 saltbush-greasewood Atriplex confertifolia-Sarcobatus vermiculatus < 35 to < 100 desert grasslands Bouteloua eriopoda and/or Pleuraphis mutica 5-100 [139] plains grasslands Bouteloua spp. 139,202] blue grama-needle-and-thread grass-western wheatgrass Bouteloua gracilis-Hesperostipa comata-Pascopyrum smithii 139,152,202] grama-galleta steppe Bouteloua gracilis-Pleuraphis jamesii 139] cheatgrass Bromus tectorum 141,199] sugarberry-America elm-green ash Celtis laevigata-Ulmus americana-Fraxinus pennsylvanica 195] northern cordgrass prairie Distichlis spicata-Spartina spp. 1-3 [139] California steppe Festuca-Danthonia spp. 139,169] western juniper Juniperus occidentalis 20-70 Rocky Mountain juniper Juniperus scopulorum < 35 Ceniza shrub Larrea tridentata-Leucophyllum frutescens-Prosopis glandulosa 139] wheatgrass plains grasslands Pascopyrum smithii 139,145,202] interior ponderosa pine* Pinus ponderosa var. scopulorum 2-30 [7,12,109] Arizona pine P. ponderosa var. arizonica 2-15 [12,44,155] eastern cottonwood Populus deltoides 139] aspen-birch P. tremuloides-Betula papyrifera 35-200 [58,195] quaking aspen (west of the Great Plains) P. tremuloides 7-120 [7,76,120] mesquite Prosopis glandulosa 118,139] mesquite-buffalo grass P. glandulosa-Buchloe dactyloides < 35 Texas savanna P. glandulosa var. glandulosa 139] black cherry-sugar maple Prunus serotina-Acer saccharum > 1,000 [195] mountain grasslands Pseudoroegneria spicata 3-40 (10**) [6,7] California oakwoods Quercus spp. 7] oak-hickory Q.-Carya spp. 195] oak-juniper woodland (Southwest) Q.-Juniperus spp. 139] canyon live oak Q. chrysolepis <35 to 200 blue oak-foothills pine Q. douglasii-P. sabiniana <35 Oregon white oak Q. garryana 7] California black oak Q. kelloggii 5-30 [139] oak savanna Q. macrocarpa/Andropogon gerardii-Schizachyrium scoparium 2-14 [139,195] little bluestem-grama prairie Schizachyrium scoparium-Bouteloua spp. 139] elm-ash-cottonwood Ulmus-Fraxinus-Populus spp. 58,195] *fire return interval varies widely; trends in variation are noted in the species reviewFire as a control method: Russian-olive sprouts after burning, but is kept at brush height with regular burning in tallgrass prairie sites in Minnesota [148,201]. According to Deiter [49], stump burning may successfully control sprouting in Russian-olive, but it is time-consuming compared to other control techniques.
Postfire colonization and spread: Observations by Caplan [34,35] suggest that mixed-species stands along the Rio Grande often become monospecific stands of Russian-olive due to vigorous root sprouting following fire. Therefore managers should be prepared to manage sprouts of Russian-olive following fire in areas where Russian-olive is present.
Preventing postfire establishment and spread: The USDA Forest Service's "Guide to Noxious Weed Prevention Practices" [185] provides several fire management considerations for weed prevention in general that may apply to Russian-olive.
Preventing invasive plants from establishing in weed-free burned areas is the most effective and least costly control method. This can be accomplished through careful monitoring, early detection and eradication, and limiting invasive plant seed dispersal into burned areas by [75,185]:
re-establishing vegetation on bare ground as soon after fire as possible
using only certified weed-free seed mixes when revegetation is necessary
cleaning equipment and vehicles prior to entering burned areas
regulating or preventing human and livestock entry into burned areas until desirable site vegetation has recovered sufficiently to resist invasion by undesirable vegetation
detecting weeds early and eradicating before vegetative spread and/or seed dispersal
eradicating small patches and containing or controlling large infestations within or adjacent to the burned area
In general, early detection is critical for preventing establishment of large populations of invasive plants. Monitoring in spring, summer, and fall is imperative. Managers should eradicate established Russian-olive plants and small patches adjacent to burned areas to prevent or limit postfire dispersal and/or spread into the site [75,185].
The need for revegetation after fire can be based on the degree of desirable vegetation displaced by invasive plants prior to burning, and on postfire survival of desirable vegetation. Revegetation necessity can also be related to invasive plant survival as viable seeds, root crowns, or root fragments capable of reproduction [75].
Managers can enhance the success of revegetation (natural or artificial) by excluding livestock until vegetation is well established (at least 2 growing seasons) [75]. See Integrated Noxious Weed Management after Wildfires for more information.
When planning a prescribed burn, managers should preinventory the project area and evaluate cover and phenology of any Russian-olive and other invasive plants present on or adjacent to the site, and avoid ignition and burning in areas at high risk for Russian-olive establishment or spread due to fire effects. Managers should also avoid creating soil conditions that promote weed germination and establishment. Weed status and risks must be discussed in burn rehabilitation plans. Also, wildfire managers might consider including weed prevention education and providing weed identification aids during fire training; avoiding known weed infestations when locating fire lines; monitoring camps, staging areas, helibases, etc., to be sure they are kept weed free; taking care that equipment is weed free; incorporating weed prevention into fire rehabilitation plans; and acquiring restoration funding. Additional guidelines and specific recommendations and requirements are available [185].
Russian-olive is native to temperate areas of Eurasia, and is adapted to the general climatic conditions that characterize much of interior western North America. Within this region Russian-olive is most invasive in semiarid riparian habitats, moist and/or irrigated pastures and meadows [41,103], and other wet or disturbed microsites such as old fields and road ditches [148]. Russian-olive's success on riparian sites may be due to its ability to tolerate a broad range of soil alkalinity, salinity, and moisture availability, and to its relative lack of specialization with respect to fluvial processes compared to native riparian species [96].
General climate: Russian-olive's primary distribution is throughout the western US, from the Pacific coast as far east as Minnesota and Kansas, and from Canada to Mexico. In this area it withstands temperatures ranging from -50 °F to 115 °F (-45 to 46 °C). Although untested, George [72] reports considerable variability in winter hardiness, depending on fall soil moisture conditions, for Russian-olive in the northern Great Plains. Large Russian-olive trunks are sometimes broken by gusty winds or drifted snow [72]. On rivers in the northern Great Plains, Russian-olive may be killed by winter ice flows [140]. According to DiTomaso and Healy [52], Russian-olive grows best in inland areas with warm summers and cold winters
In providing guidelines for growing Russian-olive, Borell [16] suggests that in areas with less than 15 inches (380 mm) mean annual precipitation (MAP), irrigation will help growth, but that Russian-olive will grow in areas with as little as 12 inches (305 mm) of precipitation. Russian-olive cuttings planted on reclaimed surface-mined sites in Wyoming had good survival rates where mean annual precipitation (MAP) ranged from 12 to 16 inches (295-402 mm). Sites with poor Russian-olive survival rates had similar site characteristics; however, MAP was 9 to 11 inches (235-271 mm) [90].
Russian-olive's ability to thrive under climatic conditions in the eastern US is less clear. According to Borell in 1971 [16], Russian-olive is grown as an ornamental in the northeast, but has not been successful in windbreak or wildlife plantings in that region, and it has been used little in the southeast. However, the USDA, Forest Service, Eastern Region ranks Russian-olive as "highly invasive", based on information from lists, botanists, and ecologists from 15 of the 20 states in that region [183]. Additionally, the Forest Service, Southern Region [184] and the Virginia Department of Conservation and Recreation [192] include Russian-olive on their lists of potentially invasive species (see Impacts).
Landscape type/land use: Russian-olive is often found in wildlands and natural areas where there are nearby or adjacent wildlife tree plantings or shelter belts that have Russian-olive in them. Sites supporting escaped Russian-olive are typically seasonally moist pastures, wetland margins, floodplains, riverbanks, shores, irrigation ditches, overflow channels, roadsides, fencerows and other disturbed sites [52,56,57,82,115,148,194]. On the Platte River in Nebraska, Russian-olive establishment is generally associated with intensively grazed wetland meadows characterized by intermittent flooding and sandy loam and silty clay soils [47]. In north-central New Mexico Russian-olive is highly invasive in lowland valley floodplains, and is typically found on streambanks and bars of rivers with highly altered hydrological regimes [128]. Russian-olive sometimes also dominates in late-successional, declining cottonwood forests on regulated rivers in New Mexico [33,91,128], Montana [2,112,140], and other western states [103].
Russian-olive also occurs along free-flowing rivers, such as the narrow bedrock canyons of the Escalante River Basin in southern Utah [15], unregulated reaches of the Yellowstone [112], the Milk, and other rivers [140] in Montana. Interestingly, Russian-olive does not always occur at the expense of native species on these unregulated rivers. Both native and nonnative species are well-represented, and native species are dominant on many sites in the Escalante Basin [15]. Similarly, where Russian-olive occurs on the upper reaches of the Yellowstone River, flooding and new channel development continuously create new cottonwood habitat [112].
Elevation/Latitude: Borell [16] reports that Russian-olive occurs from sea level to at least 8,000 feet (2,400 m) in the western U.S. Other elevations of occurrence reported by area are as follows:
Location Elevation References AZ up to 5,500 feet (1,680 m) [98] CA generally < 5,000 feet (1,500 m) [86] CO 4,500 to 6,500 feet (1,370-1,980 m) [83] ID 3,000 to 4,420 feet (909-1,340 m) [79] MT 2,100 to 3,400 feet (640 to 1,036 m) [81] NV 2,600 to 6,000 feet (790-1,830 m) [94] NM 4,775 to 5,450 feet (1,460-1,660 m) [128] WY 4,500 to 7,500 feet (1,370-2,290 m) [90] Grand Canyon region 1,850 to 3,100 feet (560-950 m) [165]
Shade tolerance, reproduction, growth, and recruitment rates for Russian-olive may vary with latitude, making it less invasive, or slower to invade at the upper and lower latitudinal limits of its North American range. While Russian-olive is frequently planted and "fairly hardy" in all but northern parts of Ontario [161], it may not be invasive at that latitude. Lesica and Miles[112] found that most Russian-olive invasions in eastern Montana occur over a period of several decades and suggest that Russian-olive may be more invasive in warmer parts of semiarid western North America. Similarly, George [72] suggests that Russian-olive does not thrive in shade in the northern Great Plains, and Borell [16] states that Russian-olive requires full sun for fruit production in "the north", but can produce fruit in the shade of large cottonwood trees in the southwest. In the Southwest, Russian-olive is most invasive in north-central New Mexico, northern Arizona, Colorado, and Utah [16]. It is not widely established in the hot deserts south of the Mogollon rim in Arizona [20], and occurs only as scattered plants along the edge of the Rio Grande River south of San Antonio, New Mexico [33].
Soils: Russian-olive thrives on a wide range of soil types and textures. Soils supporting Russian-olive are commonly Mollisols or Entisols, with textures ranging from clay loam to sand, with varying amounts of coarse fragments (e.g. [79,128]).
Soil moisture: Several reports indicate that Russian-olive favors sites with moderate to high soil moisture [36,37,47,147], and does poorly on dry sites [37,112,147]. Russian-olive was the only woodland type found on poorly drained soils on the Platte River in Nebraska [47]. Conversely, drought tolerance is part of the horticultural appeal of Russian-olive in some areas ([96], and references therein). In a central Illinois study, for example, Russian-olive survived and grew better on an upland site compared to a bottomland site [48].
Other reports indicate Russian-olive occurrence on seasonally wet sites, on a wider or intermediate range of soil moisture conditions, or at an intermediate elevation above mean river level [33,52,55,79,103,128]. For example, Russian-olive did not occur in alluvial bar sample plots on the Marias River in Montana, and was found at low density on only 2 alluvial bar plots on the Yellowstone River [112]. On young, moist terraces on these rivers, Russian-olive occurred with and without a cottonwood canopy; however, it did not occur outside a cottonwood canopy on the upper, dry terraces. The authors suggest that occurrence of Russian-olive only in riparian forests on upper terraces may be due to facilitation by the cottonwood canopy making a cooler, more humid microclimate, and/or cottonwood acting as a hydraulic pump, bringing water from the water table to the upper rooting zone ([112] and references therein). Once Russian-olive is present on these high terraces, it appears to persist after overstory cottonwoods die. In the absence of Russian-olive, many such sites would be dominated by sagebrush steppe following cottonwood senescence [112].
In New Mexico and Montana Russian-olive is classified as a facultative wetland plant - one that usually occurs in wetlands but is occasionally found in nonwetlands [81,128]. As a facultative phreatophyte, Russian-olive avoids drought stress by tapping into ground water ([96] and references therein). Russian-olive is generally reported to occur on sites where the water table is 2 to 6 feet (0.6-1.8 m) below the surface for at least part of the growing season [16,79,128]. Shafroth and others [156]found that the lowest numbers of both Russian-olive and cottonwood seedlings survived when groundwater levels were farthest from the soil surface. Compared to many native riparian trees in western North America, Russian-olive may have more drought adaptations that compensate for its relatively small root mass, including reflective silvery foliage, a relatively thick cuticle, and sunken stomata ([96], and references therein). Additionally, Klich [102] argued that morphological and anatomical leaf variation within individual Russian-olive canopies constitutes an adaptive advantage in semiarid riparian habitats characterized by strong variations in solar radiation, air temperature, and humidity.
Soil chemistry: Discriminate analysis of Russian-olive infested and uninfested sites at Utah Lake, Utah, indicated that magnesium concentration, clay content, and pH were significantly (P≤ 0.05) higher where Russian-olive occurred, and phosphorus content was significantly lower, although Russian-olive did occur on some sites with high levels (70 ppm) of phosphorus [36]. According to Borell [16] Russian-olive does not thrive in acid soils, and a pH of 6 may be the lowest limit. This has not, however, been tested and is not supported by the relative success of Russian-olive planted on acid mine spoils with pH ranging from 4.3 in California [31] to a lower limit of 5.5 on coal mine spoils throughout the eastern U.S. [193]. Conversely, Russian-olive did not survive on acid surface-mine spoil reclamation sites in Kentucky, where pH was below 4.5 and available phosphorus was generally less than 7 ppm [144].
Russian-olive is said to be better adapted than many other tree species to alkaline or saline soils [16,23,147,182]. In a laboratory study, seeds and recently germinated seedlings of Russian-olive rated as the most alkali tolerant of 20 common shelterbelt species tested for tolerance of sodium sulphate and sodium carbonate [167]. Field observations are consistent with this result, as Russian-olive is reported to be well-established on some alkaline sites ([96], and references therein).
Russian-olive seems also to be moderately to highly tolerant of salinity in experimental studies [99,124,125], and generally more tolerant of salinity than associated native species such as Fremont cottonwood [157] and plains cottonwood ([96], and references therein). A study at Utah Lake reported average soluble soil salt concentrations of 2.0g/L (range 0.1-3.5g/L) on sites supporting a noncultivated Russian-olive population, compared to an average of 5.2 g/L (range 0.7-15.0 g/L) on adjacent sites supporting saltcedar [36]. Conversely, Monk and Wiebe [124] rank Russian-olive as saline tolerant as tamarisk, and Kefu and Harris [99] cite data from Zhou (1987) indicating that Russian-olive can grow in soils with salinities of 10 to 15 g/L. However, Russian-olive seedlings planted in a highly saline (electrical conductivity (EC) 9.2 dS/m) and sodic (SAR 33.1) bentonite soil in Wyoming died within 2 weeks (Uresk and Yamamoto 1994, as cited by [96]), and Russian-olives were dead in saline meadows along the Bighorn River, Wyoming, where soils had an EC of 27.5 dS/m [2].
Number and size of nitrogen-fixing nodules on Russian-olive roots decreased with increasing concentration of sodium chloride, being significantly (P<0.05) reduced at 5 g/L NaCl. Still, symbiotic nitrogen fixation in Russian-olive shows a high tolerance of salinity and is likely to make a substantial contribution to the nitrogen requirements of Russian-olive plants even at 10 g/L NaCl [99].
Disturbance: In some cases Russian-olive invades areas where disturbance results in microsites with favorable conditions, such as road and railroad ditches, and irrigated and/or heavily grazed pastures (e.g. [47,148]). Along the Milk River in Montana and Alberta, the highest densities of Russian-olive were along the reach that had more livestock grazing and beaver harvesting, as both beaver and livestock prefer cottonwood over Russian-olive [140]. Similar observations were made by Lesica and Miles along other Montana rivers [112,113]. Russian-olive is also invasive on sites at later successional stages, due to its shade tolerance and ability to establish in intact ground cover [95,156]. Russian-olive is better adapted to the artificial flow regimes and reduced flood disturbance of regulated rivers than associated native species [50,111,112,140,156,188]. Where a dynamic disturbance regime maintains most of the active floodplain in early-successional vegetation (i.e. young to middle-aged cottonwoods and willows), only a small proportion of the riparian zone will remain undisturbed long enough to become fully stocked with Russian-olive. Russian-olive is more likely to become dominant in reaches where the riparian zone in less dynamic or where the stream is more entrenched or has been artificially channelized [96,112,148] (see Successional Status).
Impacts: There is varied and somewhat limited empirical evidence available demonstrating Russian-olive's impacts upon native ecosystems in North America; however, some evidence suggests that Russian-olive replaces native vegetation, altering vegetation structure and reducing wildlife habitat for some species. Additionally, some authors have suggested that Russian-olive can alter stream hydrology and nutrient cycling [180], although this has not been tested in natural settings.
Russian-olive is often invasive in riparian areas, which are often impacted by a plethora of human-induced disturbances. "Riparian ecosystem functions have been altered, reduced, or lost among the cascading effects of river management actions on many western rivers. Because ecosystems are complex and replete with interconnected, confounding factors, it can be difficult to quantify losses and function, and to sort out causes and effects. Riparian nonnative invasives appear to be a single symptom or facet of a complex, systemic resource allocation problem" [171].
Rankings: Several agencies and organizations rank Russian-olive as invasive to varying degrees. The USDA, Forest Service, Eastern Region ranks Russian-olive as "highly invasive" (nonnative plants that invade natural habitats and replace native species), based on information from lists, botanists, and ecologists from 15 of the 20 states in that region [183]. Conversely, Russian-olive is ranked as an "occasionally invasive species" (plants that generally do not affect ecosystem processes but may alter plant community composition by outcompeting one or more native plant species) by the Virginia Department of Conservation and Recreation. These are plants that often establish in areas severely disturbed by events such as ice storms, windthrow, or road construction, and spread slowly or not at all from disturbed sites [192]. Russian-olive is ranked as a "Category 2 species" (nonnative plant species that are suspected to be invasive or are known to be invasive in limited areas of the Southern Region) by the Southern Region of the US Forest Service, as reported by the Southeast Exotic Pest Plant Council. Category 2 species will typically persist in the environment for long periods once established and may become invasive under favorable conditions, thus posing a potential risk to the integrity of natural plant communities in parts of the region [184]. The California Invasive Plant Council (Cal-IPC) lists Russian-olive among the most invasive wildland pest plants in California. These are " documented as aggressive invaders that displace natives and disrupt natural habitats" [32]. However, there is no information in the literature specifically describing distributions and impacts of Russian-olive in California. At a given site, Russian-olive may be present as scattered individuals, within multi-species canopies, or in monotypic stands [96]. Russian-olive is said to displace and/or have the potential to displace native climax species in many parts of the western US such as the Platte River drainage of Nebraska [47] and other prairie river floodplains [140]; marshlands in South Dakota [137]; the Rio Grande Basin in New Mexico [33,91,123,128], and other river drainages in the Southwest [128].
Several characteristics give Russian-olive an advantage in the communities it invades, including high seed production and viability, seed longevity, seed dispersal by birds and mammals, vegetative reproduction following injury, drought and salt tolerance, and the ability to establish in the absence of disturbance in late successional communities (see Botanical And Ecological Characteristics). These characteristics allow Russian-olive to replace some dominant, native riparian species that can no longer germinate, establish, and persist under conditions imposed by river impoundment (e.g. increased salinity, reduced flooding, and water table declines) and other impacts of human development [4,19,45,64,81,91,111,112,113,123]. Native riparian trees tend to be pioneers, dependent on physical disturbance for recruitment [23,96,156]. Flow regulation resulting in reduced flood peaks and point bar accretion rate, in addition to land clearing, livestock grazing, beaver cutting, ice damage, and fire, along with nonnative species invasions, are all implicated in the decline of native woody vegetation in riparian ecosystems in the western US [30,61,67,134,160,171,174]. These same site conditions and processes that lead to the decline of native species concurrently provide ideal site conditions for Russian-olive establishment and eventual dominance [50,111,112,140,156,188]. Russian-olive is both a partial cause and a symptom of native species declines [91].
Once established, Russian-olive may further hinder recruitment of native cottonwood and willow on some sites [47,112]. For example, where Russian-olive occurs as a major understory component along the Rio Grande River, from Espanola to south of Belen, New Mexico, it will continue to spread through the woodland, contributing to stabilization of the riverbanks against future flooding, and thus further limit opportunities for cottonwood regeneration [91]. Similarly, in a comparison of the free-flowing Yellowstone River and the flow-regulated Marias River in eastern Montana, Lesica and Miles [111,112,113] found cottonwood establishment and dominance was not precluded by Russian-olive on the upper reaches of the Yellowstone River where flooding and new channel development continuously create new habitat for cottonwood establishment. However, cottonwood may eventually be replaced by Russian-olive on the Marias River as old cottonwoods die on upper terraces and young cottonwoods on low terraces are removed by beaver or livestock or shaded by less palatable species [111,112,113].
Russian-olive dominance may further lead to reduced species diversity. Russian-olive stands tend to be less diverse both structurally and compositionally than surrounding communities [91,128]. In Montana, for example, undisturbed colonizing and established cottonwood communities support as many as 114 and 58 plant species, respectively, compared to only 29 species in Russian-olive stands [81,140]. Altered structural and compositional plant diversity may lead to lower wildlife diversity.
Wildlife: The impact of Russian-olive invasions upon wildlife species is variable, site specific, and often debated. Also see the Importance to Livestock and Wildlife section of this report. Anecdotal evidence and observations by managers suggest that several species may be affected by Russian-olive invasion, although in some cases it is unclear whether impacts are caused by Russian-olive itself, or by changes in the ecosystem as a whole. Although Russian-olive has been promoted for use in wildlife habitat plantings, there has been relatively little research on its use by native animals [96].
Knopf and Olson [103] suggest that naturalization of Russian-olive on floodplains in the Rocky Mountains has provided additional wildlife habitat between riparian cottonwood forests and adjacent grass-dominated uplands. In some cases Russian-olive may provide important structural habitat for wildlife species by forming an intermediate-height canopy layer that is lacking in some native riparian forest communities. It may also increase the spatial extent of woody habitat by establishing on the outer edge of native riparian forests, providing additional habitats, especially for those avian species that are associated with tall shrub vegetation. Bird species richness and alpha diversity in monotypic Russian-olive stands were intermediate to those of native riparian and native upland vegetation types in Colorado, Idaho and Utah [103]. However, in some cases Russian-olive forms dense, monotypic stands that replace native communities on floodplains (see above), thus altering and potentially reducing habitat options for wildlife [91,137,140]. Some authors suggest that the displacement of native floodplain forest by Russian-olive can result in loss of habitat for species such as cavity-nesting and insectivorous birds [25,103,112,137,168].
Some researchers have examined Russian-olive's relative usefulness to wildlife as compared with native plant species it replaces, with mixed results. Several studies indicate that Russian-olive is utilized to varying degrees, and with varying degrees of success, by many avian species along the Rio Grande River [110,204], the Gila River [168], the Columbia River (Hudson 2000, as cited by [168]), and the Snake River [25]. However, results and related inference from several studies indicate avoidance of Russian-olive and/or a preference for native plant species by, for example, primary and secondary cavity nesters [168], neotropical migrants (Hudson 2000, as cited by [168]), greater prairie-chicken ([McCarthy et al 1997] and references therein), ducks [70], and foreign guilds in winter [25]. Additionally, Brown [25] found that species richness, abundance and density were greater in willow than in Russian-olive habitats, and all foraging guilds avoided Russian-olive in the breeding season along the Snake River in Idaho.
Other studies and reports indicate less certainty about the role and/or impacts of Russian-olive for native wildlife species. The threatened southwestern willow flycatcher, for example, nests in native vegetation where available but also nests in thickets dominated by Russian-olive and saltcedar, and individuals of both species are used as nesting substrates ([188] and references therein). High-elevation (>6,200 feet (1,900 m)) breeding sites are typically dominated by native trees and shrubs, although Russian-olive is a major habitat component at some high-elevation breeding sites in New Mexico. From the standpoint of flycatcher productivity and survivorship, the suitability of nonnative-dominated habitats is unknown. Flycatcher productivity is lower in nonnative dominated sites compared with native-dominated sites in some locations, and higher in others. It is unclear whether factors such as patch size may have greater effects on flycatcher productivity at those sites. Details are given in the southwestern willow flycatcher recovery plan [188]. Results presented by Kelly and others [100] and Gazda and others [70] also do not seem to support the conjecture that nonnative shrubs in riparian areas provide lower-quality habitat for birds, and Russian-olive does provide a food source for many birds. The role of Russian-olive in native wildlife habitat is unclear for many species [168,204].
For small mammals, species richness was greater in Russian-olive stands than in the native riparian and upland vegetation types (low species richness, intermediate diversity) in Colorado, Idaho and Utah [103]. Native beavers primarily use cottonwood trees while rarely using Russian-olive or tamarisk along several rivers in eastern Montana [111,112,113]. Thus, beavers create areas of lower competitive stress for Russian-olive by felling dominant cottonwoods. Most beaver damaged cottonwoods were cut off at the base, while damage to Russian-olive was usually confined to 1 or 2 basal limbs. Growth rates of both Russian-olive and tamarisk were substantially higher where beavers had reduced the cottonwood canopy cover. Managers wishing to reintroduce beavers should consider the potential effect on invasive plants; it may be best to control invasives before reintroducing beavers [113].
Hydrogeology/Nutrient cycling/Other: Some authors have suggested that Russian-olive influences hydrogeomorphic processes, for example by increasing floodplain roughness in habitats where woody vegetation would otherwise not occur (Tickner et al 2001, as cited by [96]), and contributing to stabilization of riverbanks against flooding [91]. There is not, however, literature available that addresses this issue.
As a nitrogen-fixing plant species, Russian-olive has high leaf nitrogen content [153], and leaves and leaf litter of Russian-olive tend to have higher nitrogen content than native species in the communities it invades. Thus, Russian-olive may contribute substantial amounts of additional nitrogen to invaded ecosystems ([96] and references therein). Nodular nitrogenase activity in Russian-olive varies with season and site conditions [206], thus the impacts of an Russian-olive as a novel N-fixing plant in some communities probably also vary. Royer and others [153] found slow processing rates of Russian-olive leaves (compared to natives) in some Idaho streams, and suggested that slowed litter processing might alter local and downstream aquatic communities. However, studies of degradation rates of Russian-olive leaf litter have been inconclusive regarding system nitrogen inputs. So, while invasion by Russian-olive may affect ecosystem nutrient levels, no studies have yet demonstrated this in invaded communities [96].
There is little quantitative information on the historic and present-day spread of Russian-olive, ecological factors that may limit the geographical range of Russian-olive, or its potential for range expansion in western North America. Lesica and Miles [112] approximate a 10-year lag before newly established Russian-olive individuals become reproductively mature in eastern Montana, and Katz and Shafroth [96] suggest inherently slow rates of spatial spread for species such as Russian-olive that possess relatively large, primarily vertebrate-dispersed seed. There is also no published information on competition or facilitation between Russian-olive and co-occurring species. More research is needed on these topics to better understand the potential impacts of Russian-olive in particular plant communities under specific site conditions [96].
Control: Detailed control prescriptions are beyond the scope of this review; however, an understanding of what kills or damages Russian-olive may provide insight into how Russian-olive responds to injury, and therefore its potential response to fire. For more detailed management techniques and prescriptions, refer to cited references, the Russian-olive Element Stewardship Abstract, or the Weed control methods handbook.
There is limited published research addressing effective techniques to control or remove Russian-olive from invaded sites. Caplan [34] and Edelen and Crowder [59] present case studies of effective Russian-olive control in New Mexico and Washington, respectively. Tu [180] discusses a variety of control approaches for Russian-olive and provides examples of Russian-olive management on Nature Conservancy preserves. Stannard and others [163] and Deiter [49] assess a variety of suppression methods, including mechanical and chemical approaches. Important considerations for Russian-olive management include age of Russian-olive individuals, timing relative to population establishment and seed set, size of Russian-olive populations, and site conditions, including land use.
Awareness and prevention are probably the most effective tools for managing against Russian-olive invasion. In Montana, for example, invasion by Russian-olive is relatively recent and ongoing, receiving important impetus from domestic plantings [111]. Land managers should be aware of Russian-olive in the area surrounding their management unit. If Russian-olive is present, monitoring for Russian-olive seedling establishment is an important prevention practice. Discourage adjacent landowners from planting Russian-olive if possible. When Russian-olive is already established in an area, it is important to employ control measures where they will be most effective (e.g., where the native vegetation has some chance of recovering).
Control of Russian-olive is difficult once trees are mature, so early detection and rapid response are important [49,180]. Similarly, large, well-established stands of Russian-olive are nearly impossible to eradicate throughout an entire watershed, whereas small patches of Russian-olive can be adequately controlled using a variety of control methods [180]. Additionally, removal of Russian-olive should be undertaken before seeds are fully developed to prevent further spread of seeds [49]. Stevens and Ayers [165] report that heightened awareness, modest field efforts, and early detection have resulted in the control of Russian-olive and other nonnative species in the Grand Canyon.
When planning Russian-olive control, integrating several approaches will likely be necessary, depending on the size, age, and extent of the population. Mowing, cutting, burning, excavation, spraying, girdling, and bulldozing have all been used to reduce aboveground Russian-olive biomass, with varying degrees of success. Russian-olive removal can be labor-intensive and expensive, especially in the 1st year of large-scale removal [180]. Most published accounts of effective Russian-olive suppression employ chemical treatment, either alone or combined with mechanical techniques [49]. Cultural control, in the sense of managing for natives, is an important consideration.
Russian-olive control approaches and successes may differ between riparian areas on free-flowing rivers and streams, where native species have a better chance of re-establishment, and more heavily managed areas along regulated rivers. Where a dynamic disturbance regime maintains most of the active floodplain in early-successional vegetation, only a small proportion of the riparian zone will remain undisturbed long enough to become fully stocked with Russian-olive. Russian-olive is more likely to become dominant in reaches where the riparian zone in less dynamic or where the stream is more entrenched or has been artificially channelized. Consequently, the latter are the places where control measures may have a more long-term benefit [112].
Successful long-term control of Russian-olive requires that all control sites be continually monitored and follow-up treatments applied for several years, since Russian-olive sprouts following injury [180]. Lesica and Miles [112] suggest that, because most Russian-olive invasions in eastern Montana occur over a period of several decades, eradication of mature trees every 10 years or of all plants every 30 years may be effective strategies for controlling Russian-olive in those areas. Rate of spread of Russian-olive probably varies among regions, so this approach may not be effective in some areas.
Prevention: Once established, Russian-olive is difficult to control and nearly impossible to eradicate. Therefore planting of Russian-olive should be eliminated due to its tendency to persist and spread in some areas, and the inevitable costs associated with long-term control [79,81]. Prevention involves awareness and education, working with adjacent landowners and managers to remove Russian-olive from plantings and prevent additional plantings, providing alternative species for planting in areas where Russian-olive is commonly used, managing livestock grazing to minimize damage to native species, maintaining natural disturbance regimes (i.e. seasonal flooding) in riparian areas, and minimizing other human induced disturbances.
According to the USDA, NRCS [186], seed or plants of Russian-olive are available through several suppliers throughout the US, and Russian-olive is not identified as an invasive species on their list. Similarly, Carty [39] recommends 10 drought resistant trees, Russian-olive among them, for planting. While he does mention that Russian-olive is nonnative, considered invasive, and displaces native species across much of the Southwest, he also says, "as long as it's not allowed to spread, it can fill a variety of drought resistant niches." This is the type of misinformation that land managers must contend with when discouraging individuals and organizations from planting "horticulturally desirable" species such as Russian-olive [39]. As long as this type of information and these plant products are available, prevention of new introductions is difficult.
Choosing noninvasive landscape ornamentals to plant at sites near natural areas can help prevent the spread of Russian-olive [52]. In the Southern Region, Russian-olive is classified as a "Category 2" species. Therefore planting is prohibited in areas where ecological conditions would favor invasiveness and is discouraged elsewhere. They suggest consulting the forest botanist, plant ecologist, or forest noxious weed coordinator for alternative native and/or noninvasive species [184]. Stannard and others [163] provide a list of native, woody species that could be planted instead of Russian-olive in the northern Great Plains.
The potential benefits of Russian-olive to landowners for windbreaks, soil stabilization and ornamental plantings must be weighed against potential negative impacts to native communities [140]. Winter [148] recommends working with landowners and managers to remove Russian-olive from shelter belts and tree plantings, and to recommend desirable, native species for future plantings in Minnesota.
Lack of natural regeneration of native species in western riparian areas may be due, in part, to cattle grazing in the Great Plains and cattle and elk grazing in the Southwest [134]. When browsing among the multispecies patches of seedlings that germinate on bare sediments after floods, livestock feed upon the more palatable cottonwoods and willows, thus favoring dominance of tamarisk and Russian-olive. Additionally, mature Russian-olive exhibits several traits that allow it to thrive in grazed habitats, including sharp thorns, which increase in density if the tree is cut back, and large seeds that may enhance the survival of seedlings following browsing. These adaptations may contribute to spread of Russian-olive into heavily-grazed meadows and pastures ([188] and references therein). Initial Russian-olive seedling establishment may be prevented in an area with targeted grazing, granivory (using animals that would eat Russian-olive seedlings and/or seeds), or temporary inundation [96].
Water diversion, groundwater pumping [91,170], and sand and gravel mining also impact native species regeneration in the Southwest [134,170]. Hydrologic alterations have been implicated in the widespread decline of some riparian forest types and in facilitating invasions by opportunistic nonnative species ([96] and references therein). Indeed, it is likely that reduced levels of fluvial disturbance downstream from dams favor invasion of Russian-olive [95,111,112,156]. Current interest in changing river-flow management strategies to restore native fish [151] and/or native riparian forest [123] provides hope for the possible control of invasive riparian plant species via restoration of ecosystem processes (also see FEIS review on tamarisk). At present, it is unclear how prescribed flows might influence the spread or abundance of Russian-olive. Ideally, river flow regimes designed to improve regeneration and survival of native riparian forest species will also limit the success of nonnative invaders [96].
Integrated management: Integrated management includes considerations of not only killing the target weed, but also of establishing desirable species and maintaining weed-free systems over the long-term. Factors to be addressed before a management decision is made include inventory and assessment to identify the target weed and determine the size of the infestation(s); assessment of nontarget vegetation, soil types, climatic conditions, and important water resources; and an evaluation of the benefits and limitations of control methods [129].
On Hempstead Plains in Uniondale, New York, where Russian-olive and other nonnative trees and shrubs are present, restoration has been attempted to re-establish the prairie matrix. Controlled burns, mowing, herbicides and reintroduction of native species have all been used, but no results were given [131].
Deiter [49] reports that the most effective means of Russian-olive control employs a combination of pulling out small individuals from moist soil using a weed wrench, and cutting larger individuals at ground level and then immediately applying a small amount of herbicide to the cut stumps. Similarly, Caplan [34] describes controlling small (<4 inches (10 cm) diameter) Russian-olive stems with a mulching tractor and controlling large stems with cutting and immediate application of triclopyr. Several annual follow-up applications of herbicide to the foliage of root sprouts were also required [34] (see Chemical control for more detail). In general, any initial control method requires at least some ongoing suppression of stem and root sprouts and of new recruitment from seed [59,96,163].
Physical/mechanical: Physical control techniques alone may be suitable for removal of Russian-olive seedlings and saplings, whereas control of larger individuals usually requires application of herbicide or removal of the stump by burning, since cut trees typically sprout from the roots and root crown [52].
Manually removing seedlings and saplings (<4 inches (10 cm) diameter) and their roots is an effective control method. It is most effective when soil is moist. Any remaining exposed roots should be cut off below ground level and buried [49,52,148,180].
Control is difficult once Russian-olive trees mature and populations are well-established. The most effective control method is the cut-stump herbicide treatment [34,49,148,180] (see Chemical control). Girdling and cutting are not effective controls by themselves, as trees are likely to sprout below the girdled or cut areas or along roots [49].
Techniques such as mowing, cutting, girdling, chaining, and bulldozing can suppress Russian-olive on invaded sites, although the disadvantages to such approaches can be substantial, including the necessity for frequent treatment repetition, the indiscriminate removal of other species, and severe soil disturbance [163]. Additionally, these approaches are not effective without long-term monitoring and follow-up removal of sprouts [180]. Regular cutting in Minnesota tallgrass prairie sites does not kill Russian-olive, but keeps it at "brush height" [148].
Fire: See the Fire Management Considerations section of this summary.
Biological: Research on biological control agents has not been undertaken for Russian-olive [49].
Herbivory does not seem to limit Russian-olive invasion in western North America to any great extent. Reviews indicate that few insects are found on Russian-olive [96,177]. Grasshoppers sometimes consume leaves of young trees as well as the fleshy part of the fruit, but rarely do serious damage [54].
Although domestic livestock browse Russian-olive, the observation that Russian-olive commonly invades grazed meadows and pastures suggests that herbivory does not prevent its survival or limit its spread. Additionally, Russian-olive seedling survival may be enhanced by large seed size, and Russian-olive adults possess several adaptations to deter grazers, including sharp thorns and leaves containing abundant defense compounds ([95] and references therein). On the other hand, granivory by generalist mammals (primarily house mice and deer mice) completely prevented germination of Russian-olive seeds outside of small mammal exclosures in study plots in Colorado [95].
There is a fair amount of literature on the susceptibility and/or immunity of Russian-olive to various diseases (e.g. [54,162]), although none have been proposed as a potential biological control agents.
Chemical: Herbicides may be effective in gaining initial control of a new invasion or a severe infestation, but are rarely a complete or long-term solution to weed management. Use of herbicides may be limited in natural areas, and it is suggested that native species large enough to provide "good structure" be present to fill the niche left by removed Russian-olives [148]. See the Weed control methods handbook for considerations on the use of herbicides in natural areas and detailed information on specific chemicals and techniques. Herbicides that have been reported as effective at controlling Russian-olive to varying degrees include glyphosate, imazapyr, triclopyr, picloram, and 2,4-D.
Foliar spraying of herbicide has provided "successful control" of Russian-olive in some cases, although long-term response is unclear. This approach may be neither feasible nor desirable in many riparian settings ([96] and references therein) due to potential effects on nontarget species, and potential for overspray or drift when applied to large stands [180]. Small seedlings can also be killed with foliar applications of a mixture of picloram and 2,4-D [148]
Cut-stump herbicide treatments can be effective if the cut surface is treated with herbicide immediately after cutting. Cuts should be made as close to the ground as possible [49,52,148,180]. In an 80-acre (32 ha) cottonwood gallery forest on the Middle Rio Grande in New Mexico, Russian-olive is the codominant tree in mixed stands. From November 1998 through February 1999, Russian-olive less than 4 inches (10 cm) in diameter were mowed, using mulching tractors, larger trees were cut with chainsaws, and triclopyr ester was applied to the cut stump within 5 minutes of cutting. A second pass was made with mulching tractors to pulverize the remaining tree waste. By summer, 1999, Russian-olive root sprouts occurred throughout the site. Numerous root sprouts were found within close proximity of larger, sprayed stumps, suggesting that the rate of triclopyr used was not effective on stumps exceeding 8 inches (20 cm) in diameter. Triclopyr was applied to leaves of Russian-olive root sprouts each year for 3 subsequent summers. Each follow-up treatment required fewer people and less time. Continued monitoring and spot treatments keeps Russian-olive under control at the site [34].
For trees that do not have to be removed or immediately taken down, exposing more than 50% of the cambium by cutting into the bark with a saw or ax close to ground level and introducing herbicides into the exposed areas is also effective [49]. Deiter [49] reports that injecting herbicide capsules around base of trunk has also been successful for controlling Russian-olive. When injecting herbicides into the cambium of a standing tree, monitoring should occur during the same year to ensure that the entire tree is affected [49].
Conversely, Edelen and Crowder [59] propose killing the top-growth with herbicide (imazapyr), followed by mechanical control of resprouts as an effective alternative to cutting and then mowing resprouts. A project to test this control approach was begun in August 1996 in south-central Washington [59], and resulted in a 90% kill rate (personal communication from Crowder as cited by [180]).
Monitoring for sprouting from cut stumps and/or roots, or seedling establishment should be done for several years following treatment [34,148,163].
Cultural: In all cases of Russian-olive control, it is important that desirable plant species be planted or otherwise cultivated to discourage re-establishment of Russian-olive. Additionally, promotion of natural processes (e.g. natural flooding regimes) may be important to manage for desirable native species. In areas where natural disturbance processes still function, removal of Russian-olive may facilitate recovery of native species. On regulated rivers and areas with intensive livestock grazing, removal or suppression of Russian-olive is likely to be only temporary, unless measures are taken to promote establishment and persistence of native species. Stannard and others [163] and Brock [20] provide lists of species useful for replacement of Russian-olive and rehabilitation of Russian-olive-infested sites.
In southwestern riparian ecosystems, managing for native species may be more successful than managing against nonnative species [171]. Elimination of the stresses, such as high salinity and reduced stream flows, that favor nonnative plants over native plants may be necessary if native plant communities are to be sustained ([188] and references therein). Stromberg and Chew [171] provide some constructive options for restoring functionality to southwestern desert riparian ecosystems. They also indicate that it is unlikely that nonnative species will be eradicated from southwestern riparian systems, but that it is also unlikely that simply removing nonnatives would allow natives to thrive where conditions no longer favor them [171]. Along these lines, Stromberg [170] discusses the ecology, threats and recovery potential of cottonwood and willow in southwestern riparian systems. See the FEIS review on tamarisk for more information on this subject.
Obedzinski and others [134] suggest that in the case of dams and diversions, we may need to accept that a return to natural, sustainable conditions may not be possible, and that we may need to design management techniques, such as timed interval flooding and artificial seedbeds, to maintain riparian function. We may also need to learn the silvics of nonnative species and utilize them according to where they best fit into riparian systems [134].
Domestic livestock browse young Russian-olive trees [16], (Katz personal observation as cited by [96]), but adult Russian-olives deter browsers with sharp thorns and defense compounds in the leaves (Seastedt personal communication as cited by [96]). Rabbits may eat the bark of small trees. Poultry (chickens, turkeys, ducks, pigeons) may eat the leaves from newly planted trees [16].
Russian-olive has been promoted for plantings to benefit wildlife because it produces abundant, edible fruit, and several native birds and mammals have been reported to use Russian-olive for food, nesting, and cover [10,16,43,77,106,108,140,143,172,175]. Borell [16] reports that more than 50 kinds of birds and mammals eat the fruit of Russian-olive. Of these, 12 are game birds, including ring-necked pheasant, grouse, mallard, quail, wild turkey, and mourning dove. Most birds swallow the fruit whole, while some peck the pulp from the seed. Seeds sprouting on the ground in spring are also readily eaten. Other wildlife known to eat Russian-olive fruit include cottontail, fox squirrel, ground squirrel, elk, and deer [16]. Squirrels also eat Russian-olive bark and young branches [172]. Pocket gophers occasionally feed so heavily on the roots of young trees that the trees die. Rodents seldom damage the bark or roots of mature trees [16]. Granivory by generalist mammals (primarily house mice and deer mice) completely prevented germination of Russian-olive seeds outside of small mammal exclosures in study plots in Colorado [95]. Lists of species observed using Russian-olive native riparian and upland sites are provided by Knopf and Olson [103].
While Russian-olive is said to provide nectar for bees (Hayes 1976, as cited by [96]), reviews suggest that insects are found only at low densities on Russian-olive [16,96,177], and that the fruit is not consumed by insects [191]. Dix and others [54] suggest that grasshoppers sometimes consume leaves of young trees as well as the fleshy part of the fruit.
It has been suggested that while Russian-olive can enhance wildlife habitat for some species, it is used to a lesser degree than native vegetation [52]. This may have greater impacts on species such as cavity-nesting and insectivorous birds on sites where Russian-olive replaces formerly dominant cottonwood and willow (see Impacts and Succession). Additionally, native beaver rarely harvest Russian-olive trees, and the severity of beaver damage was low compared to the mortality and damage inflicted to native plains cottonwood on the Marias [111], lower Yellowstone, Bighorn [113], and Milk rivers [140] in Montana.
Palatability/nutritional value: Hansen and others [81] rank palatability of Russian-olive as poor for cattle, domestic sheep, and horses; with moderate energy and protein values. They rank food value or degree of use as fair for elk, white-tailed deer, and pronghorn; poor for mule deer; and good for upland game birds, waterfowl, small nongame birds, and small mammals [81].
Russian-olive's palatability to livestock and wildlife species in several western states has been rated by Dittberner and Olson [53] as follows:
CO MT ND UT WY Cattle Poor Fair Fair Poor Poor Sheep Fair Fair Good Fair Fair Horses Poor Poor Poor Poor Poor Pronghorn ---- Fair ---- Fair Poor Elk ---- ---- ---- Good Fair Mule deer ---- Poor Poor Good Good White-tailed deer Good Fair ---- ---- Poor Small mammals Good ---- ---- Good Good Small nongame birds Good Good Fair Good Good Upland game birds ---- Good Good Good Good Waterfowl ---- ---- ---- Fair Good
A study of the nutritional energetic requirements of sharp-tailed grouse recommends Russian-olive fruit as good winter food [62]. Another report says that Russian-olive helps provide grouse with a winter diet sufficient to survive winter conditions in the northern Great Plains ([63] and references therein).
Seasonal proximate composition and cell wall constituents (%) of Russian-olive leaves harvested in northern Pakistan are given as follows [11]:
Season dry matter crude protein neutral detergent fiber acid detergent fiber hemicellulose acid detergent lignin ash Spring 65.6 14.9 37.5 21.0 16.5 2.5 7.1 Winter 46.7 13.9 31.0 20.8 10.2 5.8 11.8
Cover value: According to Borell [16], Russian-olive has spreading, thorny branches and thicket-forming growth that make excellent wildlife cover. Mourning doves, mockingbirds, roadrunners, and several other kinds of birds are said to use Russian-olive for nesting [16]. According to Stubbendieck and others [172], Russian-olive provides winter roosting cover for ring-necked pheasants and nesting sites for mourning doves and songbirds in the Great Plains. Some Southwestern willow flycatcher nesting sites are found in riparian habitats dominated by nearly monotypic stands of tamarisk and Russian-olive in the Southwest [188].
Hansen and others [81] rank thermal or feeding cover value of Russian-olive as fair (moderately used for cover when available) for elk and mule deer, and good (readily utilized for cover when available) for white-tailed deer in Montana. They rank thermal or feeding cover value as good for upland game birds and small nongame birds, and fair for waterfowl and small mammals [81].
The following description of habitat types and plant communities in which
Russian-olive occurs is taken from examples found in the literature. The objective
is to provide examples of vegetation types in which it occurs, and is not meant to
imply that Russian-olive is restricted to these types within these areas. Most examples
come from areas where Russian-olive is most widespread and most invasive. In some areas,
particularly the eastern U.S., there is little to no information on vegetation types
in which Russian-olive occurs.
In the northwestern U.S., Russian-olive was introduced primarily for use in
windbreaks and it has established outside of cultivation in several places [87]. In central
Washington, where a sagebrush (Artemisia spp.) steppe site was transformed into a
mitigation wetland, Russian-olive occurs with common cattail (Typha latifolia),
bulrush (Scirpus spp.), common reed (Phragmites australis), and purple
loosestrife (Lythrum salicaria) [89]. At Hanford in south-central Washington,
several species of trees were planted as windbreaks and shade for irrigated farmland.
Some of the more commonly occurring tree species include black locust
(Robinia pseudoacacia), Russian-olive, cottonwood (Populus spp.), mulberry
(Morus spp.), sycamore (Platanus spp.), and poplar (Populus spp.).
Although introduced to this area, these trees now provide habitat for a variety of wildlife,
including nest sites, and hiding and thermal cover. Some species (e.g., cottonwood, poplar,
and Russian-olive) have established along the Columbia River and are considered by some as
"functional components" of these riparian areas [116]. Russian-olive occurred
throughout irrigated Kentucky bluegrass (Poa pratensis) and orchardgrass
(Dactylis glomerata) pastures in southeastern Oregon [101].
Russian-olive occurs throughout California; however, no information was found
describing native plant communities affected by Russian-olive. It occurs primarily in
disturbed, sometimes moist places in the San Joaquin Valley, San Francisco Bay Area,
eastern Sierra Nevada, Modoc Plateau, and parts of the Mojave Desert near springs [49,52,86].
It was used for mine spoil reclamation at a site supporting Jeffrey pine (Pinus jeffreyi),
white fir (Abies concolor), and mountain big sagebrush (Artemisia tridentata ssp.
vaseyana) dominants [31]. Russian-olive is most common in horticultural settings and interior
riparian areas in California [32].
Russian-olive was planted as an ornamental in the Intermountain area, and has
occasionally escaped onto roadsides and along lower elevation streams [46]. On wetland sites
along the Yakima River in south-central Washington, thickets of Russian-olive have replaced
stands of black cottonwood (Populus balsamifera ssp. trichocarpa) and native willows
(Salix spp.) [59]. Hansen and others [81] describe a Russian-olive community type
in Montana. In the Rocky Mountains, foothills, and intermountain valleys, the Russian-olive
community type represents seral stages of many different vegetation types including
ponderosa pine/red-osier dogwood (Pinus ponderosa/Cornus sericea) and Rocky Mountain
Douglas-fir (Pseudotsuga menziesii var. glauca)/red-osier dogwood habitat types.
Isolated stands are found in western Montana, such as near Dillon, Thompson Falls, and in
the Flathead Valley near the National Bison Range [81].
Russian-olive is widespread throughout the Great Basin [127] where it occurs in a
variety of plant communities on a variety of site types. It is common and widespread
throughout most of Nevada, in wet to damp sites of sagebrush deserts [94]. Hall and Hansen
[79] describe an incidental Russian-olive community type that typically forms stringer
communities on upper floodplain terraces adjacent to streams and rivers at the
bottom of deep canyons at low elevations in southern and eastern Idaho. It may also be found
in low depressional areas capable of retaining water near the surface for much of the year,
especially potholes and abandoned river oxbows. Russian-olive stands in Idaho may be associated
with black cottonwood in open communities with widely spaced individuals. The shrub component
may be sparse or robust depending on local site factors, and may include willow, Wood's rose
(Rosa woodsii), hawthorn (Crataegus spp.), and currant (Ribes spp.).
Graminoids, particularly quackgrass (Elymus repens), foxtail barley (Hordeum jubatum),
and Kentucky bluegrass, may dominate the herbaceous understory. The forb component is often poorly
represented and includes bulrush and cattail (Typha spp.) on wet sites, and Rocky Mountain
iris (Iris missouriensis) and Eaton's aster (Symphyotrichum eatonii) on drier sites.
Hall and Hansen [79] report the canopy cover of various native and nonnative plant species recorded
in mid- to late-seral stands of the Russian-olive community type in Idaho. Knopf and Olson [103]
describe a Russian-olive-dominated site along the Snake River where riparian vegetation
is mostly dominated by black cottonwood, willow, and Wood's rose; and upland vegetation is
dominated by big sagebrush (A. tridentata). The Russian-olive site consisted of mature
Russian-olive, about 30 feet (10 m) tall, with canopy cover exceeding 80%. Cheatgrass
(Bromus tectorum) and a few scattered shrubs such as black greasewood
(Sarcobatus vermiculatus) and Wood's rose occurred in canopy openings and in the understory.
A shallow wetland with cattails and bulrushes bordered the north side of the stand [103]. Along the
middle Snake River, from Swan Falls Dam to the Idaho/Oregon border, Russian-olive and tamarisk make
up approximately two-thirds of the tree species present. In this area Russian-olive occurs
primarily with sandbar willow (Salix exigua), peachleaf willow (S. amygdaloides),
and tamarisk in the zone 3 to 5 feet (0.8-1.4 m) above mean river level [55].
Russian-olive has escaped cultivation and established along drainages and in moist meadows
over vast areas of Utah [198]. Christensen [41] describes it as a conspicuous part
of the vegetation in pastures, along fences and ditch banks, and in moist lowlands in the
valleys of central and northern Utah. A riparian site along the Uinta River in northeastern
Utah supported a Russian-olive stand with about 50% canopy cover comprised of individuals
mostly 16 to 20 feet (5-6 m) tall, with several mature trees up to 33 feet (10 m) tall. The
understory was dominated by cheatgrass and forbs, especially mustards (Brassica spp.),
and occasional alfalfa (Medicago sativa) plants. A native riparian site in the
area was dominated by cottonwood associated with willows, scattered Russian-olive and
occasional saltcedar (Tamarix ramosissima and/or T. chinensis). Upland vegetation
in the area was dominated by big sagebrush, green rabbitbrush (Chrysothamnus viscidiflorus),
cheatgrass, Indian ricegrass (Achnatherum hymenoides), and several forbs, especially
desert princesplume (Stanleya pinnata) and lupine (Lupinus spp.) [103]. At Utah Lake,
a comparison of infested and uninfested sites revealed that sites infested with Russian-olive
also supported plant species typical of mesic meadows, especially perennial grasses. A variety
of understory communities was associated with Russian-olive. Plant species consistently associated
with Russian-olive include bearded wheatgrass (Elymus trachycaulus ssp. subsecundus),
redtop (Agrostis gigantea), common ragweed (Ambrosia artemisiifolia), and
tanseyleaf aster (Machaeranthera tanacetifolia) [36]. In the Escalante River Basin in southern
Utah, Russian-olive occurs with tamarisk, Fremont cottonwood (Populus fremontii), and willow [15].
Russian-olive is common throughout the Southwest, especially along rivers on the
Colorado Plateau and other high elevation sites, including the Rio Grande and San Juan
rivers [188]. It is well established and continues to spread in the Four Corners region
[20]. Habitat and plant community information comes primarily from these areas, although
individual or scattered occurrences are also indicated in other areas such as in critical
desert tortoise habitat in the Mojave and Colorado deserts [21].
Dick-Peddie [50] describes a "successional-disturbance riparian" vegetation type
in New Mexico, with 2 series. The Russian-olive series is most common in the northern
part of the state, and the saltcedar series is more common in the southern part [50]. In a
130-mile (210 km) stretch along the Rio Grande River, in north-central New Mexico from Espanola
to Bernardo, Russian-olive occurs within one of the most extensive gallery forests
of Rio Grande cottonwood (Populus deltoides ssp. wislizenii) remaining in the
Southwest, where Rio Grande cottonwood comprises over 93% of the canopy trees, and peachleaf
willow and Goodding willow (Salix gooddingii) comprise the remainder of the canopy trees.
Sandbar willow, Russian-olive, saltcedar, Great Plains false willow (Baccharis salicina),
desert false indigo (Amorpha fruticosa), and New Mexico olive (Forestiera pubescens
var. pubescens) are dominant understory shrubs. Desert grasslands, shrubland, residential
areas, agricultural fields, and levee roads surround the woodland boundaries [91]. Along a more
southerly stretch of the Rio Grande River, between Albuquerque and El Paso, Russian-olive is rare
south of San Antonio, New Mexico. It occurs in communities dominated by cottonwood with Goodding
willow and tamarisk as codominants; and in communities with a dense overstory of cottonwood and a
separate stratum of Russian-olive and Goodding willow, with tamarisk present on adjacent, disturbed
sites. Other plant species in these communities include desert false indigo, yerba mansa
(Anemopsis californica) and sweetclover (Melilotus spp.), with no grasses [33].
Muldavin and others [128] describe a Russian-olive alliance that occurs in lowland regions of
the Rocky Mountains with detailed descriptions of its occurrence in New Mexico. In New Mexico,
the alliance is widely distributed in the middle Rio Grande, Pecos, and San Juan river basins.
Russian-olive stands are often represented by densely forested thickets, often with greater than
90% total canopy cover, and some scattered mature Rio Grande cottonwood in the canopy. The authors
describe 4 provisional community types within the alliance (3 on the Middle Rio Grande, and 1 on
the San Juan River) where Russian-olive is the dominant indicator species, and suggest that additional
information is needed on the composition and ecology of these community types throughout the West.
The Russian-olive/alkali sacaton (Sporobolus airoides) community type is an open-canopied
woodland that often takes on a shrubland appearance due to mowing. Other common native wetland
trees and shrubs in this type include Goodding willow, sandbar willow, and Great Plains false
willow. Herbaceous cover is grassy and dominated by alkali sacaton and occasionally codominated by
saltgrass (Distichlis spicata) and alkali muhly (Muhlenbergia asperifolia).
Smooth horsetail (Equisetum laevigatum) is a common wetland forb in this community.
The Russian-olive/sandbar willow community type has a dense canopy of Russian-olive with sandbar willow
in the understory. Understory herbaceous species are variable, and often dominated by mesic forbs and
grasses. In the Russian-olive/sparse community type, Russian-olive forms nearly impenetrable stands
with scattered sandbar willow and saltcedar in the shrub layer and sparse undergrowth. Herbs are mostly
represented by scattered bunches of grasses that may include purple threeawn (Aristida purpurea),
saltgrass, Baltic rush (Juncus balticus), and alkali sacaton. These stands form as narrow strips
ranging from 30 to 100 feet (10-30 m) wide along lowland riverbanks. Flood control structures such as
jetty jacks are also present and may have influenced the establishment and maintenance of the community.
The Russian-olive/redtop community type and is found on lowland river bars on the San Juan River in
northwestern New Mexico. Shrubs are usually poorly represented in this community type, and may include
sandbar willow or saltcedar. The herbaceous layer is dominated by the nonnative invasive grass redtop,
with a wide variety of other mesic forbs and grasses. Wetland indicators in this type include field horsetail
(Equisetum arvense), reed canarygrass (Phalaris arundinacea), common reed,
common threesquare (Schoenoplectus pungens var. pungens), owlfruit sedge
(Carex stipata), common cattail, and wild mint (Mentha arvensis) [128].
Russian-olive also codominates with Rio Grande cottonwood in several New Mexico riparian
community types. On some sites, where absence of flooding may contribute to Russian-olive
invasion, it forms a sprawling subcanopy under a dense, closed canopy of Rio Grande cottonwood.
In the Rio Grande cottonwood-Russian-olive/New Mexico olive community type, Russian-olive
reproduces under the dense canopy and may be replacing New Mexico olive on some sites. The
Rio Grande cottonwood-Russian-olive/tamarisk community type is widespread in the middle Rio
Grande and San Juan river basins, and is characterized by a mixed-tree canopy with Rio Grande
cottonwood dominating the overstory and Russian-olive in the understory. Saltcedar is well
represented to abundant, and dominates the shrub layer. Overall species diversity is poor in
this community type [128]. Russian-olive also occurs in the subcanopy of the Rio Grande
cottonwood/big sagebrush community type in the San Juan River Basin in northwestern New Mexico
and probably adjacent Utah and Arizona. It may also reproduce and become invasive in the
understory of Rio Grande cottonwood/Goodding willow communities in the Pecos and Rio
Grande basins [128].
Similarly, in a cottonwood/Russian-olive type described by Hink and Ohmart (1984, as cited by [67]),
Russian-olive formed a monotypic understory with herbaceous plants being sparse to absent. In
the northern reaches of the Middle Rio Grande, a cottonwood/juniper (Juniperus spp.) type
was characterized by an understory of juniper mixed with Russian-olive, New Mexico olive, threadleaf
snakeweed (Gutierrezia microcephala), and rubber rabbitbrush (Chrysothamnus nauseosus).
They also recognized a Russian-olive community type dominated by young to intermediate-aged
Russian-olives interspersed among patches of young sandbar willow, cottonwood, saltcedar,
and seepwillow (Baccharis salicifolia) with a dense herbaceous layer of mixed grasses
and forbs (Hink and Ohmart 1984, as cited by [67]). A survey conducted by Mount and others [126]
in 1995 indicates an increase in cover, height, and density of Russian-olive in the Middle Rio Grande
over the 11 years since Hink and Ohmart's study. In the Gila River Valley in southern New Mexico,
Russian-olive occurs both as isolated understory trees within riparian patches composed of Fremont
cottonwood, Goodding willow, Arizona sycamore (Platanus wrightii), boxelder (Acer negundo),
Arizona walnut (Juglans major), velvet ash (Fraxinus velutina), Great Plains
false willow, and Arizona alder (Alnus oblongifolia); and in small monotypic stands on the
periphery of patches [168].
Russian-olive occurs throughout the Great Plains, but is most common in the western
half of the region. Originally planted in shelterbelts, it is one of the hardiest species of trees
introduced to the Great Plains and has persisted and spread in many areas, especially in the
understory along rivers and streams [172,197]. Deserted homesteads in the Great Plains and the
western slope of the Rocky Mountains are often recognizable by persisting windrows of Russian-olive
trees [197].
Hansen and others [81] describe an Russian-olive riparian plant community type as an incidental
type at low elevations on floodplains of the major rivers and streams in central and eastern
Montana. Relatively large stands of this community type are found along the
Yellowstone River and its major tributaries, along the Musselshell River near Roundup, in
irrigated valleys around the Bowdoin National Wildlife Refuge near Malta, along the Milk River
from Glacier National Park to Glasgow, along the Missouri and Sun rivers near Great Falls, and
on the Charles M. Russell National Wildlife Refuge north of Lewistown [81]. About 500 Russian-olive
saplings and seedlings were introduced directly to the Milk River in Montana and Alberta floodplain in
1950. Secondary growth has since formed thickets so dense that other riparian species have been
excluded. Downstream from the point of introduction, Russian-olive and plains cottonwood
(Populus deltoides ssp. monilifera) are scattered on the floodplain and commonly
associated with Wood's rose, peachleaf and sandbar willow, buffaloberry (Shepherdia spp.),
smooth brome (Bromus inermis), and Canada thistle (Cirsium arvense); while silver
sagebrush (Artemisia cana), western wheatgrass (Pascopyrum smithii), and
needle-and-thread grass (Hesperostipa comata) occupy the most elevated and driest sites
on alluvial fans between the floodplain and valley slopes [140].
On many sites Russian-olive forms thickets such that it excludes most other species. Dense stands
of Russian-olive tend to limit access by livestock. However, severe grazing can cause the understory
to be dominated by nonnative herbaceous species such as Kentucky bluegrass and timothy
(Phleum pratense). In stands that are somewhat open, associated species may include widely
scattered plains cottonwood, green ash (F. pennsylvanica), boxelder, peachleaf willow,
narrowleaf cottonwood (Populus angustifolia), and/or an assortment of grasses and
forbs [81]. Adjacent upland or drier sites may be dominated by the silver sagebrush/western wheatgrass
habitat type and a variety of upland species. Wetter sites may be dominated by common cattail, bulrushes,
spikerushes (Eleocharis spp.), or common reed habitat types, or by peachleaf willow
or sandbar willow community types [81,113]. Cottonwood forests may be hundreds of meters wide in
meandering reaches of the rivers [113]. Russian-olive also occurs in riparian plant communities dominated
by green ash, chokecherry, plains cottonwood, red-osier dogwood, western snowberry
(Symphoricarpos occidentalis), and Wood's rose in Montana. In the northern Great Plains,
the Russian-olive community type may represent a seral stage of the green ash/chokecherry
(Prunus virginiana) habitat type or the boxelder/chokecherry habitat type [81].
At the confluence of the Knife and Missouri rivers in north-central North Dakota,
native forest sites are composed of plains cottonwood (73.9% of the density), and peachleaf
willow (24.2%), with 1.9% Russian-olive, which occasionally invades openings within these forests
[42]. At Nature Conservancy preserves in Minnesota, Russian-olive occurs in tallgrass
prairie sites (especially those that are grazed or otherwise disturbed), riparian areas,
and savannas. Here it may affect threatened species such as western prairie fringed orchid
(Platanthera praeclara), grape fern (Botrychium spp.), small white lady's
slipper (Cypripedium candidum), Hill's thistle (Cirsium hillii),
greater prairie-chicken, dakota skipper, and upland sandpiper [148].
Russian-olive cuttings planted on surface-mined reclamation areas in Wyoming had
good survival in plant communities dominated by western wheatgrass, bluebunch wheatgrass
(Pseudoroegneria spicata), needle-and-thread grass, blue grama (Bouteloua
gracilis), Sandberg bluegrass (Poa secunda), big sagebrush, Saskatoon serviceberry
(Amelanchier alnifolia), Gambel oak (Quercus gambelii), quaking aspen
(Populus tremuloides), snowberry (Symphoricarpos spp.), chokecherry, and
mountain brome (Bromus marginatus). Sites with poor Russian-olive survival (0 to 40%)
were dominated by more xeric species, such as bottlebrush squirreltail (Elymus elymoides),
rabbitbrush (Chrysothamnus spp.), basin wildrye (Leymus cinereus), shadscale
(Atriplex confertifolia), Gardner's saltbush (A. gardneri), and winterfat
(Krascheninnikovia lanata) [90].
Russian-olive occurs mostly on low ground along streams or valleys and scattered in agricultural
areas of Colorado, probably originating from cultivated plants [83]. On a study site
northwest of Milliken, Russian-olive occurs in a stand with canopy cover of about 40% and trees
16 to 26 feet (5-8 m) tall. Cheatgrass, Canada thistle, and stinging nettle (Urtica dioica)
dominate the understory, and a few small Siberian elm (Ulmus pumila) are also present. Along
the south side of the Big Thompson River, on a site characterized by an overstory of plains cottonwood
and an understory primarily of grasses, with common cattail, bulrushes, and willows present in small numbers,
scattered Russian-olive occurs infrequently on drier microsites away from the main river channel [103].
Russian-olive is considered a dominant indicator species on the Platte River in Nebraska
[47]. Here its average canopy cover is 12.3% to 24.5% and it typically codominates with plains
cottonwood. In Russian-olive/plains cottonwood vegetation types, important understory species
include common ragweed, sedges (Carex spp.), saltgrass, and Kentucky bluegrass. Plains
cottonwood/Russian-olive vegetation types tend to occur on drier somewhat upland sites, and are
characterized by an overstory of large plains cottonwood and an dense understory of Russian-olive,
green ash, and Missouri River willow (Salix eriocephala). Understory shrubs are
infrequent, but in a few locations roughleaf dogwood (Cornus drummondii) is an important
component. Russian-olive occurs, with an average of 6.2% cover, in plains cottonwood/eastern
redcedar (J. virginiana) communities associated with riverbank grape (Vitis riparia),
Wood's rose, green ash, and desert false indigo with Kentucky bluegrass and poison-ivy
(Toxicodendron radicans) as major herbaceous species. It occurs in cottonwood shrub
communities with 2.2% cover. In some areas along the Platte River, Russian-olive forms dense,
nearly monospecific stands [47].
Along the Arkansas river in western Kansas, Russian-olive occurred with skunkbush
sumac (Rhus trilobata), desert false indigo, and green ash on some sites [73].
There is very little information on Russian-olive's occurrence in the eastern U.S.
Russian-olive is grown as an ornamental in the northeast [16]; however, reports of its occurrence
in natural communities are rare. On Hempstead Plains in Uniondale, New York, Russian-olive occurs
with other woody species such as eastern white pine (Pinus strobus), black cherry
(Prunus serotina), and shining sumac (Rhus copallina) among small pockets of native
plant communities dominated by bluestems (Schizachyrium scoparium, Andropogon virginicus,
and A. gerardii), switchgrass (Panicum virgatum), indiangrass (Sorghastrum nutans),
yellow sedge (Carex pensylvanica), and staggerbush (Lyonia mariana) [131]. In
Virginia, Russian-olive occurs in mesic environments, in sun or part shade, on coastal plain, piedmont,
and mountain sites [192].
In Canada, Russian-olive is often planted as an ornamental in Nova Scotia [150],
and is "frequently planted and fairly hardy" in all but northern parts of Ontario [161],
but there is no information available regarding its distribution in native plant communities.
Russian-olive community types are described in the following publications:
Montana [81]
southern and eastern Idaho [79]
New Mexico [128]
Russian-olive has been promoted for many uses including, for example, windbreaks and erosion control [41,71,72,84]; snow traps [158]; gully and streambank plantings; hedgerows and living fences; attracting wildlife [38,41,77,84]; ornamental and landscape plantings [39]; and nectar for bees (Hayes 1976, as cited by [96]). It has been used as a nurse crop for black walnut (Juglans nigra) because of its nitrogen fixing ability [48]. Russian-olive has been planted on reclaimed mine spoils in central and eastern U.S. [24,144,193], Wyoming [90], and California [31]. It is planted in coastal areas because of its ability to withstand ocean salt spray and deposition of windblown sand (Morehart et al 1980, as cited by [96]). Russian-olive was used as part of an introduced seed mixture in a study of revegetation techniques in a northwestern Colorado disturbed big sagebrush community in 1976 [132]. Russian-olive has since been declared a noxious weed in Colorado [189].
Public and private agencies have continued to advocate planting Russian-olive for windbreaks and other horticultural purposes. As recently as the 1980s and 1990s, many state and federal agencies were subsidizing the distribution of Russian-olive seedlings in the western US and Canada [78,137]. Additionally, planting recommendations and suppliers of seedlings such as those given by Borell [16] are often found in the literature. Russian-olive was among the most popular tree species offered by nurseries throughout the United States from 1980 to 1986, and was especially popular in the north-central and western regions. Its popularity decreased significantly (chi-square test, alpha=0.05) in the north-central region between 1980 and 1986. Reasons for decreased popularity are not given or speculated upon [133].
Continued horticultural interest in Russian-olive is evidenced by recent research addressing such topics as chemically regulating the growth of Russian-olive in nurseries to maintain a compact form, herbicide resistance of Russian-olive seedlings, treatments that facilitate rooting in Russian-olive cuttings, and methods of propagating Russian-olive from leaf segments and shoot segments ([96] and references therein).
Russian-olive leaves were found to be an accurate biomonitor for lead, cadmium, and zinc in heavy metal-contaminated soils in Turkey; heavy metal concentrations in leaves correlated well with heavy metal concentrations in surface soils [3].
A literature search indicates several references suggesting medicinal properties of Russian-olive; however, that topic is beyond the scope of this review.
Wood Products: Russian-olive wood makes good fuel and fair fenceposts [16].
Russian-olive branches elongate each year by growth from a lateral bud near the terminus of the previous year's growth [112]. There are no reports in the literature on when spring growth begins in different regions. Dates of flowering and fruit maturation are reported by area as follows:
Area Flowering date Fruit maturation Refs CA May-June [130] Illinois May-June [122] Nevada April-June [94] New Mexico May-June [115] TX June August-October [191] central plains May-June September [164] Great Plains May-June [172] Intermountain area May-July [46] northeastern US June-July [74] western North America May-June September-November [52]
Russian-olive seed dispersal occurs throughout fall and winter, with ripe fruits remaining on trees throughout the winter or until consumed by animals [16,200]. Fruits are borne from 4 to 20 feet(1-6 m) or more above ground and are thus available to animals above deep snow [16].
There is no information in the literature specifically addressing the response of Russian-olive to fire. Several workers report that Russian-olive sprouts from the trunk, root crown, and/or roots after top-kill or damage [34,49,52,59,112,140,148,172], and some report sprouting from roots and root crown following fire [20,35,201].
Observations by Caplan [34,35] suggest that mixed species stands along the Rio Grande often become monospecific stands of Russian-olive due to vigorous root sprouting following fire. Mount and others [126] surveyed vegetation in an area along the Middle Rio Grande from Albuquerque to Belen and found evidence of 31 fires in the study area between 1984 and 1995. On burned polygons, the 1st woody species to establish or sprout was sandbar willow, followed by saltcedar, Russian-olive, and, finally, Rio Grande cottonwood [126].
The hard-coated seed of Russian-olive may require scarification for germination (see Germination), suggesting the possibility of fire scarification. However, this has not been reported in the literature.
Russian-olive reproduces by seed and postinjury sprouting.
Breeding system: Flowers are perfect, or some are staminate [46,86,172,198].
Pollination: Fragrant yellow flowers are produced in spring and are insect pollinated [52,96].
Seed production: It is generally stated that Russian-olive produces a large amount of seed, but nothing quantitative was found in the literature. According to Borell [16], the age at which Russian-olive produces its 1st seed crop varies with latitude, but seedlings typically produce fruit about 3 to 5 years after transplanting. Lesica and Miles [112] recorded the ages of fruit-bearing Russian-olive on the Marias and Yellowstone rivers in Montana. None of the Russian-olive trees sampled on the Marias River under age 5 produced fruit, while all trees over age 14 fruited. On the Yellowstone River only 1 of 38 plants ≤ 6 years old fruited in 1998. Fruiting generally began at 7 to10 years of age, and 89% of Russian-olive over 10 years old produced fruit. These results suggest the average age of 1st reproduction for Russian-olive on both rivers is around 10 years [112].
Seed dispersal: Most Russian-olive fruits remain on trees until distributed by animals, especially birds, mostly during the fall and winter. Seed may also be dispersed by water or ice.
Several bird species consume Russian-olive fruit [16,47,138], and at least some are known to defecate viable seed [101]. For example, European starlings are effective dispersers of Russian-olive in southeastern Oregon and may have contributed substantially to its spread there. Kindschy [101] observed large flocks of European starling foraging throughout the winter on Russian-olive fruit in irrigated grass meadows in southeastern Oregon. The starlings then roosted in larger trees such as black cottonwood and Siberian elm, dispersing Russian-olive seed below. When tested, there was no significant loss of viability (P<0.05) in seeds that passed through the digestive tract of starlings [101].
Fruit loosened by wind or feeding birds may also fall to the ground [16] where other vertebrates consume and cache Russian-olive fruit (personal observations cited by [96,113,138]), sometimes up to 500 feet (150 m) from the original sources (F. Johnson personal communication, as cited by [138]). While DiTomaso and Healy [52] indicate that Russian-olive seeds survive ingestion by animals, the only experimental evidence of this is from Kindschy's study [101] of European starlings. Lesica and Miles [113] observed raccoons eating Russian-olive fruits and dispersing seed in their feces, although viability of these seeds was unknown.
Russian-olive seed may also be dispersed by fluvial transport [20,96,113,140]. Lesica and Miles [113] indicate that ripe fruits will float for up to 48 hours. Additionally, observations and evidence presented by Pearce and Smith [140] suggest seed dispersal by water and ice transport, although this was not tested directly and is not documented elsewhere in the literature.
Seed banking: Russian-olive seed stored under "ordinary" conditions remains viable for up to 3 years [136], but seed longevity in the field is undocumented [52]. Russian-olive seeds are dispersed during the late fall and winter in a dormant state and require a period of after-ripening to break dormancy [80,88]. Several researchers have studied Russian-olive seed dormancy (see Germination); however, exact mechanisms of dormancy are unknown.
If seeds retain viability for a long period, Russian-olive may be able to exploit suitable germination conditions over a relatively long time compared to native taxa with which it commonly associates. Success of Russian-olive may be due, in part, to its ability to germinate whenever conditions at a particular site become suitable [156]. More research is needed to determine longevity of Russian-olive seed banks.
Germination: Russian-olive seeds are hard and dormant at maturity and require a period of cool, moist stratification, or possibly scarification, for germination.
Laboratory tests indicate that a period of 2 to 3 months at around 41 °F (5 °C) under moist conditions is required to break Russian-olive seed dormancy [88,176,200]. Dormancy appears to be related to inhibitors found in all parts of Russian-olive seeds [80,88,92]. Activity of the inhibiting substance was not reduced by low temperatures; however, an uncharacterized substance that may reverse inhibition was produced after exposure to low temperatures. Activity of the inhibiting substance was also reversed by gibberellic acid and kinetin [80]. Jinks and Ciccarese [92] found that 6 days of washing before prechilling, or warm, moist stratification for 4 weeks (without prechilling) improved germination, suggesting that the inhibitor is somewhat water-soluble [92].
It has been suggested that scarification may improve germination rates of hard-coated Russian-olive seeds [20,52]. Laboratory tests indicate that dormancy is broken by soaking in sulfuric acid [200], (Heit 1967, as cited by [92]). The dormancy period was reduced in cleaned seed compared to that of dry fruits [136], suggesting that digestion of fruits may also break dormancy.
Some reviews indicate that Russian-olive seeds germinate in many soil types and over a variable period of time, depending on site conditions [52,103], and that Russian-olive seeds germinate under a broader range of conditions than seeds of native willow and cottonwood associates [52]. In greenhouse experiments, Shafroth and others [156] found that Russian-olive seeds germinate under a wide variety of moisture conditions at different times of the growing season, and that seed germination varies under different treatment combinations of light and elevation above groundwater. Russian-olive seedlings suffered little to no mortality following germination [156].
Seedling establishment/growth: Observational and experimental evidence indicates that Russian-olive seedlings can establish on disturbed sites in full sun (e.g. [2,112]), in shade, or within intact groundcover. These nonspecific establishment requirements confer an advantage on Russian-olive over associated native species that require full sun and disturbance for establishment [52,96] (see Successional Status).
Older stands of Russian-olive in Montana generally have plants of many ages, indicating that infrequent disturbance events are not required for recruitment [112]. Katz and others [95] found that seedlings of Russian-olive established within dense, undisturbed herbaceous vegetation on experimental plots, while those of cottonwood did not. Kindschy [101] observed Russian-olive growing throughout irrigated Kentucky bluegrass and orchardgrass pastures in southeastern Oregon. The author suggests that the large seed of Russian-olive contains sufficient food resources to enable sprouting roots to penetrate sod to mineral soil and thus establish in these areas [101].
DiTomaso and Healy [52] indicate that Russian-olive seedlings can survive under a canopy of mature willows and cottonwoods and then grow quickly when the loss of a tree creates an opening in the canopy, although the source of this information is not given. Conversely, willow and cottonwood seedlings seldom survive under a canopy of Russian-olive trees. Shafroth and others [156] found that artificial shade decreased growth of plains cottonwood seedlings more than Russian-olive seedlings in experimental planters but that there was no effect on seedling survival of either species. Russian-olive's ability to establish in the shade may vary with latitude [16,72] (see Site Characteristics).
Russian-olive growth may be independent of many environmental variables. Lesica and Miles [112] measured Russian-olive recruitment and growth rates in 46 stands on the Marias and Yellowstone rivers in Montana. Russian-olive recruitment rate per mature tree in 46 stands varied from 0 to 4.07 recruits/year, with a mean of 0.69 recruits/year. There was no difference in recruitment rate between the Marias and Yellowstone rivers. There was no significant relationship between recruitment rate and tall-tree canopy cover (r²=0.006, P=0.61). There was also no relationship between Russian-olive recruitment rate and associated understory vegetation; nor between recruitment rate and elevation above September river levels for either the Marias or Yellowstone rivers [112].
Growth: Russian-olive is said to have a slow [81] to rapid [16] growth rate. There is little experimental evidence to support these observations; however, growth rate probably varies with site conditions such as temperature, moisture, and light availability, as well as plant age.
In warm areas, Russian-olive seed planted in spring will produce bushy plants 2 to 3 feet (0.6-0.9 m) tall in the 1st season. Under "good" conditions, nursery transplants may reach 4 to 5 feet (1.2-1.5 m) in the 1st year, and 8 to 12 feet (2-4 m) in the 2nd year [16]. Borell [16] suggests that under dry land conditions in the Great Plains, Russian-olive's growth rate is probably half that. Under "prevailing climatic conditions" in the northern Great Plains, planted Russian-olive averaged 12.8 feet (4 m) tall after 10 years with 96% survival, and averaged 16 feet (5 m) tall after 44 years, with 51% survival [72]. On abandoned farm land in Michigan, planted Russian-olive was 17 feet (5 m) tall, with 83% survival after16 to 18 years [77]. Growth rate was negatively associated with height above the September river level for both the Marias (r²=0.20, P=0.028) and Yellowstone (r²=0.18, P=0.012) rivers in Montana. There was no relationship between growth rate of Russian-olive and composition of understory vegetation, although there was a significant negative relationship between Russian-olive growth rate and cottonwood canopy cover (r²=0.06, P=0.002, n=153) [112].
Lesica and Miles [112] found that growth rate (measured by height) of Russian-olive increased with age over all age classes on riparian sites on 2 rivers in Montana. Growth rate varied between 0.1 and 2.7 cm/year with a mean of 0.8 cm/year, and was not different between the 2 rivers when corrected for age. Recruitment and growth were not affected by stand age as reflected by understory vegetation; however, growth, but not recruitment, was greater on lower sites closer to alluvial groundwater [112]. Rankings for biomass production, short- and long-term revegetation potential, and erosion control potential provided by Hansen and others [81] also suggest that Russian-olive's growth rate increases with age. They also suggest that Russian-olive produces a relatively high yield of dry plant material and is relatively persistent.
Asexual regeneration: It has been suggested that Russian-olive spreads by "underground rootstalks" [18]; however, there is no evidence in the literature that indicates that Russian-olive spreads by asexual reproduction under field conditions, except following injury or top-kill. According to Williams and Hanks [200] Russian-olive can establish by layering, and it is propagated by stem and root cuttings and by grafting for horticultural purposes [200]. Brock [20] observed Russian-olive branches that were covered with sediments had numerous adventitious roots on buried stem portions. The occurrence of Russian-olive establishment from stem or root pieces in the field is unclear.
Several workers report that Russian-olive sprouts from the trunk, root crown, and/or roots after top-kill or damage [34,49,52,59,112,140,148,172], and some report sprouting from roots and root crown following fire [35,201]. There is no information in the literature specifically addressing asexual regeneration in Russian-olive after fire.
Russian-olive can establish at early successional stages, on bare, nutrient poor soils, and at later successional stages, under a well-developed canopy. It can persist into later stages of succession and change successional trajectories in the native communities that it invades. For example, it grows equally well beneath a dense cottonwood overstory, in almost pure stands of tamarisk, and in open areas along the Rio Grande River in New Mexico [33,91]. Knopf and Olson [103] observed naturalized Russian-olive individuals growing both within cottonwood floodplain forest and colonizing open wet meadows in several western states. It also occurs (as seedlings, saplings, and mature trees) in cottonwood forests of all ages, from the relatively open canopies of young (5- to 29-year-old) stands to very old (>80-year-old) stands along the Bighorn River in Montana [2].
Early succession: As a nitrogen-fixing, actinorrhizal plant, Russian-olive is likely to be an early-successional, pioneer species, able to colonize nitrogen-poor soils such as sandy, eroded mineral soils and wetlands [40]. As such, Russian-olive has often been used for reforestation and mine reclamation [24,31,90,144,193]. Russian-olive can establish in the postflood environment, but does not tend to dominate on sites with frequent flood disturbance [112].
There is no information in the literature regarding postfire succession in Russian-olive; however, observations by several workers indicate that Russian-olive sprouts from roots and root crown following aboveground damage [34,35,59,163,201], and is therefore likely to colonize on-site in the initial postfire community. If Russian-olive has a persistent seed bank and heat resistant or heat scarified seed, Russian-olive seedlings may also establish in the early postfire environment. More research is needed in this area of Russian-olive's reproductive ecology.
Late succession: The large seed size of Russian-olive provides resources to help seedlings establish under mature canopies. This allows Russian-olive regeneration in riparian areas to be decoupled from flood disturbance, unlike associated native species that depend on seasonal flooding for seedling establishment. Russian-olive is especially able to take advantage of the reduced levels of physical disturbance that characterize riparian habitats downstream from dams [23,96,156] (see Impacts).
Field observations indicate that Russian-olive is relatively tolerant of interference from established native vegetation, invading beneath woody overstories or within herbaceous vegetation [2,16,47,91,101,103,188]. Russian-olive has been recorded growing and reproducing in the understory of mature riparian forests along the Platte River in Nebraska [47], the Rio Grande River in New Mexico [33,60,66,91],and several rivers in Montana [2,111,112]. In fact, along the Marias and Yellowstone rivers in Montana, invasion of riparian communities often depends on proximity to established, mature trees [112].
Understory invasion in mid- and late-successional communities may alter the fuel structure of those communities (see Fire Ecology).
Shade tolerance: Russian-olive grows in either full sunlight or shade, but seems to prefer full sunlight (Cote and others 1988, as cited by [20]). It can establish and persist both in the shade of a mature overstory, in partial shade in margins and gaps, and in the open under full sunlight (see above). Shade tolerance may vary with latitude, although these limits are unclear. It has been suggested that Russian-olive does not thrive in shade in the northern Great Plains [72] or produce fruit in shade in "the north" [16]. Shade tolerance at northern latitudes may be related to age of Russian-olive and to moisture availability.
In eastern Montana, Akashi [2] observed Russian-olive seedlings at all overstory ages along the Bighorn River, though individuals seemed to persist in margins and gaps. On the Marias and Yellowstone rivers, Russian-olive was restricted to the cottonwood understory on dry high terraces but occurred with and without a cottonwood canopy on moist, lower-elevation terraces. Lower terraces along open and little-shaded channels, ditches and other relatively wet sites also provide habitat conducive to Russian-olive establishment and invasion [112].
Succession on Russian-olive-infested sites: Invasion of Russian-olive may alter the successional dynamics of riparian forests in several ways. In much of interior western North America, native riparian forests are dominated by pioneer species (primarily cottonwood and willow species) that are generally intolerant of shade [156] and do not establish within intact vegetation [95]. Russian-olive invades these communities by establishing beneath the canopy of native riparian trees and forming self-replacing stands. Russian-olive also establishes on flood-disturbed sites that are optimal for cottonwood recruitment.
On many western rivers, the absence of fluvial disturbance and lack of recruitment of native riparian trees allows Russian-olive to establish and eventually dominate on many sites at various successional stages [91,96,97,111,112,156]. Invasion of a cottonwood-dominated riparian forest by Russian-olive might proceed as follows on a river system with reduced flood magnitude and frequency: 1) Russian-olive seedlings establish under, or in margins or gaps of the canopy of an existing stand of cottonwoods; 2) as cottonwoods die, Russian-olive becomes the dominant overstory species; and 3) recruitment of Russian-olive seedlings continues in the shade of the new canopy, but cottonwood recruitment is restricted to the narrow, frequently-disturbed margins of the active stream channel, where annual high flows may bury or scour seedlings [156]. In addition to flow regulation, livestock grazing and trampling and selective harvesting by beaver limit recruitment of cottonwood on river floodplains in the northern Great Plains [111,113,140]. Shafroth and others [156] predict that Russian-olive will likely become a more prominent component of western landscapes as the cottonwood canopy of existing stands along regulated rivers is replaced by Russian-olive now present in the understory.
A review by Lesica and Miles [112] describes natural succession on the Marias and Yellowstone rivers in eastern Montana as follows: Cottonwood and willow establish from wind-borne seed on fresh, moist alluvium deposited by floods or channel meandering. Terraces with an understory of willow and a ground layer of hydrophytic plants are dominated by relatively young cottonwoods. As stands became older, periodic deposition raises the ground level higher above the water table. These older stands support an understory dominated by less hydric shrubs and grasses. After 100 to 200 years, cottonwoods die and are replaced by sagebrush or shade-tolerant green ash. Russian-olive may affect this riparian successional sequence by persisting and continuing to reproduce on these upper terraces and dominating the plant community after overstory cottonwoods die. Russian-olive was common along both rivers in stands with plants of many ages, suggesting that Russian-olive, but not cottonwood, recruitment continues to occur under established Russian-olive trees. Conversely, cottonwood establishment and dominance is not precluded on sites where flooding and new channel development continuously create new cottonwood habitat [15,112].
Concentrations of Russian-olive have been observed and mapped on most eastward flowing rivers in Montana, including unregulated rivers. Along the unregulated stretch of Milk River in Montana and Alberta, for example, Russian-olive outnumbers plains cottonwood on many sites between the Alberta/Montana border and the Fresno reservoir [140]. Cottonwood seed dispersal and germination do not appear to be a problem on unregulated reaches, as there were twice as many cottonwood as Russian-olive seedlings; however, successful cottonwood recruitment occurs only once in 5 to 10 years on the Milk River (Bradley and Smith 1986, as cited by [140]). In their study reach, Pearce and Smith [140] estimated attrition from seedling to sapling at 73% for cottonwood and 12% for Russian-olive. Based on present recruitment rates, it appears that Russian-olive will outnumber cottonwood in all size classes along the Milk River study reach within 10 years [140].
In the eastern Great Plains, cottonwood and willow are early successional species and are replaced by a self-sustaining, diverse hardwood forest as natural succession proceeds. In the western Great Plains, forest diversity decreases westward until only the early-successional tree species, cottonwood and willow, remain. Thus, in much of the western Great Plains, the climax native bottomland community is not forest, but shrubland or grassland. Therefore, maintenance of riparian forest in this area is dependent on regular physical disturbance. Since the 1800s, fire suppression and decreases in flow variability caused by water development have allowed Russian-olive and trees from the eastern Plains, especially green ash and eastern redcedar, to establish and persist in western bottomlands where shade-tolerant trees were formerly absent ([68], and references therein). Currier [47] provides an illustration and discussion of successional patterns on the Platte River in Nebraska. In some areas cottonwood dominates the forest canopy while Russian-olive establishes in the understory. Without cottonwood regeneration, Russian-olive, juniper, or mixed hardwood species eventually dominate the forest vegetation. Where Russian-olive establishes in grasslands in this area, sites become progressively elevated and drier over time as a result of overbank deposition, degradation of the river channel, and declines in river stage levels. The oldest Russian-olive stands were found on deep, well-drained soils, on which Russian-olive is apparently no longer able to establish [47].
Along the Rio Grande River in New Mexico, introduction of tamarisk and Russian-olive has changed the successional stages and ultimate dominants in many communities. Russian-olive replaces screwbean mesquite (Prosopis pubescens) in the understory of large Rio Grande cottonwood in phreatophyte communities along the Rio Grande south of Socorro [33], and may be replacing New Mexico olive on more northerly sites [128]. For more information on the effects of Russian-olive on succession in southwestern riparian areas see Habitat Types and Plant Communities.
Longevity: Along the Marias and Yellowstone rivers in eastern Montana, Russian-olive occurred in all size classes along both rivers, and most stands were multiple-aged. The oldest Russian-olives recorded were 36 and 40 years old on the Marias and Yellowstone rivers, respectively. Mean age of Russian-olive stands was 15.3 years on the Marias and 18.6 years on the Yellowstone. The oldest Russian-olive tree was as old or older than the oldest cottonwood in 39% and 14% of the stands on the Marias and Yellowstone rivers, respectively. In many cases these were stands where cottonwoods appeared to have established in fresh alluvium deposited on existing terraces with established Russian-olive [112].
Russian-olive has a low recruitment rate on eastern Montana rivers, and requires about 10 years to reach reproductive maturity; thus, invasion should proceed slowly compared to other aggressive herbaceous or shrubby weeds. Russian-olive has been present on both of the rivers studied for 36 to 40 years, but density in many stands is low [112].
The currently accepted name for Russian-olive is Elaeagnus angustifolia
L. (Elaeagnaceae) [46,51,74,87,93,94,98,107,161,194,197,198].
According to Vines [191] and Weber and Wittman [197], several varieties of
Russian-olive are known in cultivation, and differ primarily in
leaf size and shape [191].
One variety described in the western literature,
E. a. var. orientalis, is treated as a separate species
by Flora USSR (1949, as cited by [9]). Flora Europaea recognizes no
varieties or hybrids of Russian-olive [178].
Daryarpaq iydə (lat. Elaeagnus angustifolia) — İydəçiçəklilər fəsiləsinin iydə cinsinə mənsubdur.
45 növ ağac və meyvə kolundan yabanı halda 2 növü yayılmışdır. İydə yabanı halda Şimali Qafqazın şərq rayonlarında, Azərbaycanın Kür və Araz çaylarının kənarlarında geniş sahələr tutur. Bu bitkinin yararlı mədəni sortları Azərbaycanın aran hissələrində olduqca çoxdur.
İydə 3–7 m hündürlükdə olur. Yabanı iydənin hündür və kol halında bitən formaları vardır. Yabanı ağacları balaca tikanlıdır. Yarpaqları uzunsov-oval, yaşıl-gümüşü rəngdədir.
May-iyunda çiçəkləyir. Çiçəkləri ətirli olub, 1-3 ədəd yarpaq qoltuğunda açılır. Dördləçəklidirlər. Ləçəyin xarici hissəsi parlaq gümüşü, iç hissəsi sarıdır. 4 erkəkciyi və bir dişiciyi vardır. Iydənin meyvələri sentyabr-oktyabrda yetişir. Çəyirdəyinin üzərini meyvənin unlu ətliyi bürüyür. Çəyirdəyi uzunsov-oval şəklindədir, ətliyi şirin və azacıq turşumtuldur. Yabanı iydələrin meyvələri dadsız və gər olur. Meyvəsinin qabığı boz sarı, tünd darçını, qırmızı rəngdə olur. Unlu ətliyə yapışmır, yeyiləndə kənar edilir.
Iydənin meyvəsi çox qidalı və uzun müddət saxlanılmağa davamlıdır. Ətliyi meyvəsinin 52%-ni təşkil edir. Tərkibində 40% şəkər, o cümlədən 20% fruktoza, 10% üzvi turşu, rəngləyici maddələr, kalium və fosfor duzları vardır. Yarpaqlarında 350 mq% C vitamini, oduncaq qabığında və çəyirdəyində isə alkaloid vardır. Meyvəsi təzə halda yeyilir, ondan hazırlanmış unu çörəyə, şorbaya və başqa yeməklərə qatırlar. Təzə meyvələrindən spirt alırlar. 100 kq iydədən 13 litr spirt almaq olar.
Qarın xəstəlikləri üçün iydə unundan hazırlanmış horra olduqca xeyirlidir. Iydə həm də balverən bitkidir.[1]
İkiləpəlilər ilə əlaqədar bu məqalə qaralama halındadır. Məqaləni redaktə edərək Vikipediyanı zənginləşdirin. Daryarpaq iydə (lat. Elaeagnus angustifolia) — İydəçiçəklilər fəsiləsinin iydə cinsinə mənsubdur.
45 növ ağac və meyvə kolundan yabanı halda 2 növü yayılmışdır. İydə yabanı halda Şimali Qafqazın şərq rayonlarında, Azərbaycanın Kür və Araz çaylarının kənarlarında geniş sahələr tutur. Bu bitkinin yararlı mədəni sortları Azərbaycanın aran hissələrində olduqca çoxdur.
İydə 3–7 m hündürlükdə olur. Yabanı iydənin hündür və kol halında bitən formaları vardır. Yabanı ağacları balaca tikanlıdır. Yarpaqları uzunsov-oval, yaşıl-gümüşü rəngdədir.
May-iyunda çiçəkləyir. Çiçəkləri ətirli olub, 1-3 ədəd yarpaq qoltuğunda açılır. Dördləçəklidirlər. Ləçəyin xarici hissəsi parlaq gümüşü, iç hissəsi sarıdır. 4 erkəkciyi və bir dişiciyi vardır. Iydənin meyvələri sentyabr-oktyabrda yetişir. Çəyirdəyinin üzərini meyvənin unlu ətliyi bürüyür. Çəyirdəyi uzunsov-oval şəklindədir, ətliyi şirin və azacıq turşumtuldur. Yabanı iydələrin meyvələri dadsız və gər olur. Meyvəsinin qabığı boz sarı, tünd darçını, qırmızı rəngdə olur. Unlu ətliyə yapışmır, yeyiləndə kənar edilir.
Iydənin meyvəsi çox qidalı və uzun müddət saxlanılmağa davamlıdır. Ətliyi meyvəsinin 52%-ni təşkil edir. Tərkibində 40% şəkər, o cümlədən 20% fruktoza, 10% üzvi turşu, rəngləyici maddələr, kalium və fosfor duzları vardır. Yarpaqlarında 350 mq% C vitamini, oduncaq qabığında və çəyirdəyində isə alkaloid vardır. Meyvəsi təzə halda yeyilir, ondan hazırlanmış unu çörəyə, şorbaya və başqa yeməklərə qatırlar. Təzə meyvələrindən spirt alırlar. 100 kq iydədən 13 litr spirt almaq olar.
Qarın xəstəlikləri üçün iydə unundan hazırlanmış horra olduqca xeyirlidir. Iydə həm də balverən bitkidir.
L'arbre del paradís,[1] arbre argentat,[2] olivera de Bohèmia o cínamom[2] (Elaeagnus angustifolia) és una espècie d'arbre caducifoli del gènere Elaeagnus.
Normalment és un arbust espinós o un petit arbre que arriba a fer de 5 a 7 m d'alt. La copa és ampla i arrodonida. Les fulles són simples, de disposició alternada, lanceolades, de 4 a 9 cm de llarg i d'1 a 2,5 cm d'ample, de color verd grisós per sobre i argentades per sota. Flors axil·lars, en grups d'1-3, argentades per fora i de color groc crema per dins, erectes i aromàtiques. Tenen forma acampanada i 4 estams; apareixen a principi d'estiu. El fruit és una drupa d'1 a 1.5 cm de llarg, ovoide, amb un llarg peduncle, de color marró vermellós, comestible i de gust agradable. El tronc sol presentar formes retorçades, i l'escorça, de color fosc, presenta una textura clivellada.
És un arbre originari de l'oest i el centre d'Àsia, sud de Rússia i del Kazakhstan a Turquia. Sembla que es va començar a conrear el 1736, a Alemanya. De llavors ençà ha estat introduït a moltes altres zones, com el sud d'Europa i de Nord-amèrica, on s'ha naturalitzat. En alguns d'aquests llocs se la considera una planta invasora. A la península Ibèrica el trobam normalment, en conreu i de forma aïllada. Un dels únics bosquets espontanis d'aquesta espècie es localitza al terme municipal de Valdemoro, al parc denominat "Bolitas del Airón". Creix sobretot en indrets secs, formant petits bosquets o de forma aïllada, barrejada amb altres espècies arbustives. Com totes les espècies del gènere Elaeagnus realitza la fixació de nitrogen a través de les arrels, fet que li permet créixer en terrenys molt pobres.
Pot créixer a diversos tipus de sòls i ubicacions, tot i que prefereix els indrets assolellats i els sòls ben drenats. Resisteix perfectament la proximitat del mar, i aguanta temperatures mínimes de fins a -40 °C. Presenta també una gran tolerància a la sequera, l'alcalinitat i la salinitat. Es pot reproduir fàcilment a partir de llavors, però també de forma vegetativa, a partir d'esqueixos. Es tracta d'un arbre de creixement ràpid.
És un arbre molt usual en jardineria, valorat sobretot pel seu caràcter ornamental: les seves fulles argentades contrasten vivament amb el color verd d'altres espècies. Molt indicat per situacions costaneres, per la seva tolerància a la salinitat. La seva capacitat per fixar nitrogen al sòl és també interessant, ja que permet incrementar el rendiment d'altres fruiters.
Els seus fruits, quan són madurs, tenen un sabor força agradable. Per altra banda, són una rica font de vitamines (especialment A, C i E) minerals i flavonoides. L'oli essencial obtingut de les seves flors s'utilitza en perfumeria. D'aquest arbre se'n pot extreure també una goma que s'utilitza a la indústria tèxtil.
La seva fusta és dura, de gra fi, i s'utilitza per fer talles, mànecs d'eines, bigues, etc. També constitueix un excel·lent combustible.
El seu nom comú és degut a la seva identificació (correcta o no) amb un dels arbres presents a l'Edèn del que es parla a la Bíblia. També se'l coneix amb el nom de "olivera de Bohèmia" per la seva semblança amb aquest arbre i al fet de ser abundant en aquella regió.
Pel que fa al seu nom científic, sembla que Carl von Linné el va triar basant-se en les paraules gregues "eleia" (olivera) y "agnos" (aloc, una planta que s'assembla, teòricament, a l'arbre). Altres fonts asseguren que el nom prové de la mateixa paraula grega "eleia" i de la també grega "gennao" (engendrar quelcom semblant), indicant així la seva semblança a l'olivera. El segon terme ("angustifolia") fa referència a la poca amplada de les seves fulles.
Al seu hàbitat
Vista de l'arbre
Il·lustració
Com a bonsai
Elaeagnus angustifolia
L'arbre del paradís, arbre argentat, olivera de Bohèmia o cínamom (Elaeagnus angustifolia) és una espècie d'arbre caducifoli del gènere Elaeagnus.
Hlošina úzkolistá (Elaeagnus angustifolia) je prastará kulturní rostlina, strom nebo keř, pocházející z oblastí Kavkazu, Střední Asie, Mongolska a střední Číny. Je nejdéle se vyskytujícím druhem rodu hlošina v české přírodě.
Z míst svého původu se hlošina úzkolistá šířila západním směrem podél karavanních cest a do Evropy doputovala již v 16. století. Dovezena byla též do Severní a Jižní Ameriky.
Vyrůstá nejčastěji na písčitých půdách a je tolerantní k suchu a k vyššímu obsahu soli v půdě. Nejlépe se jí daří na plném slunci v propustných půdách s dostatkem vápníku. Má bohatý kořenový systém, který je využíván ke zpevňování pohyblivých písčitých zemin. Je odolná vůči vnitrozemským mrazům. V Kašmíru roste v nadmořské výšce až 3500 m. Za vhodných podmínek dokáže rychle obsadit široký prostor.
Tato vytrvalá opadavá dřevina vyrůstá jako široký a hustý keř nebo jako strom vysoký 3 až 10 m. Stromy s často pokřiveným kmenem s červenohnědou odlupující se kůrou mívají široce kuželovitou korunu. Keře vytvářejí husté, pro lidí téměř neprostupné houštiny. Letorosty, list i plody jsou porostlé chlupy vytvářejícími charakteristické stříbřité zbarvení. Větvičky jsou v mládí stříbřitě šupinaté, chlupaté a často trnité, později zhnědnou. Jsou hustě porostlé střídavě vyrůstajícími, čárkovitými, kopinatými až úzce vejčitými listy s krátkým řapíkem; celokrajné čepele mívají dlouhé 4 až 10 cm a široké 0,5 až 4 cm. Listy jsou zpočátku oboustranně stříbřité, později se na lícní straně zabarví šedozeleně.
V úžlabí starších listů vyrůstají jednotlivě, nebo až po třech, silně voňavé, žlutavé květy. Jsou krátce stopkaté, oboupohlavné nebo jen prašníkové a měří až 1 cm v průměru. Mají čtyřčetný, zvonkovitý nebo trubkovitý a 1 cm dlouhý kalich který je vně stříbřitě chlupatý a uvnitř žlutý. Koruna není vyvinutá. V každém květu jsou čtyři tyčinky s krátkými nitkami nesoucí podlouhlé prašníky. V oboupohlavných květech je dále podlouhlý jednodílný semeník s jediným vajíčkem a zakřivená čnělka zhruba stejně dlouhá jako kalich. Kvetou v květnu a červnu, opylovány jsou hmyzem, hlavně včelami, které v květech nacházejí hodně pylu i nektaru. Ploidie druhu bývá 2n = 12 nebo 2n = 28.
Plod je elipsoidní, soudečkovitá, zprvu zelená a šedá, později červenohnědá, stříbřitě chlupatá nepravá peckovice asi 1,5 cm velká. Obsahuje podlouhlou tvrdou pecku a moučnou dužinu která postupně sládne. Plodí již od časného mládí a dožívá se až 100 let. Rozmnožuje se semeny (peckami), která do okolí roznášejí hlavně ptáci požírající plody a rychle odnožujícími kořenovými výběžky.
Hlošina úzkolistá má v současnosti v evropských podmínkách význam hlavně jako okrasná rostlina. Odolává městskému smogu, soli v půdě a příliš jí nevadí okolní zpevněné plochy, je proto používána v městské výsadbě. Bohužel problematický je její pyl, který je silným alergenem. Vysazuje se též za účelem zpevňování zasolených písčitých půd a dobře roste i v blízkosti moře. Vůbec nejvhodnější je výsadba její keřovité formy do středních dělících pásů na dálnicích.
V místech původu se hlavně zpracovávají plody. Z čerstvých se vyrábějí aromatické kompoty, marmelády i likéry, sušené se melou na mouku z které se vaří kaše a pečou cukrovinky. Usušené plody obsahují cukr a lze je dlouho skladovat. Pevné dřevo se v bezlesých krajinách používá na výrobu domácího nářadí i na topení.
V roce 1830 počala být vysazována v Pensylvánií ve Spojených státech amerických jako rostlina mající rekultivovat půdu po důlní těžbě. Velmi se tam uchytila a zakrátko se počala invazně šiřit po okolí. Vyskytuje se již v Maine, Virginií i Wisconsinu. Využívá své schopnosti jímat v symbióze s půdními bakteriemi kořeny vzdušný dusík a obohacovat jím půdu. Vytváří neprostupné porosty a vytlačuje původní floru, poskytuje však úkryt i potravu pro drobné savce i ptáky. Pokusy o vypalování skončily vyrašením spousty nových výhonů.[2][3][4][5] [6]
V okrasném zahradnictví se někdy používá. Habitus je nepravidelný, koruna řídká, nepravidelně se rozkládající, zahušťující zmlazujícími výhony. Dřevina podrůstá výmladky do okolí, je zcela nevhodná na menší plochy a málo vhodná na udržované plochy. Pravidelný řez by byl žádoucí, ale vyvolává silnější podrůstání z kořenů.
Toxikologické informační středisko řadí plody hlošiny úzkolisté mezi „téměř nejedovaté plody“, o nichž uvádí, že nebezpečná může být dávka nad 20 plodů (bobulí, semen); po větším požitém množství se podává aktivní uhlí; nebývá nutná hospitalizace (jen u mimořádně citlivých osob při závažných příznacích); u zdravých jedinců se objevují nanejvýš zažívací potíže[7]
Starý kmen
Větev s květy
Květy a listy
Dozrávající plody
Obrázky, zvuky či videa k tématu hlošina úzkolistá ve Wikimedia Commons
Hlošina úzkolistá (Elaeagnus angustifolia) je prastará kulturní rostlina, strom nebo keř, pocházející z oblastí Kavkazu, Střední Asie, Mongolska a střední Číny. Je nejdéle se vyskytujícím druhem rodu hlošina v české přírodě.
Smalbladet sølvblad (Elaeagnus angustifolia) er et lille, løvfældende træ eller en stor busk. Nektarmængden er kun lige tilstrækkelig til, at bierne kan overleve at besøge arten. Planten er stærkt salttolerant.
Væksten er bred og uregelmæssig, ofte flerstammet. Hovedgrenene er vandrette til opstigende. Barken er først hvid med et tæt hårlag. Senere bliver den blank og rødbrun med lyse korkporer. På samme tid vil aborterede sideskud være omdannet til stive torne. Gamle grene og stammen får til sidst en gråbrun bark, som strimler op på langs.
Knopperne er spredte, tæt behårede og uden egentlige knopskæl. Bladene er smalt ovale med grågrøn overside og sølvhvid underside. Blomstringen sker i juni, hvor der ses talrige, gule blomster i bladhjørnerne. Frugterne er sølvgrå, behårede stenfrugter med stribet kerne.
Rodnettet består af en dybtgående pælerod med et stærkt forgrenet siderodnet. Træet har samliv med en slægt af strålesvampe (Frankenia), som danner N-samlende knolde på rødderne. Rodvæksten indledes før løvspring og afsluttes først efter løvfald.
Højde x bredde og årlig tilvækst: 8 x 8 m (35 x 35 cm/år).
Træet er udbredt på lysåbne, tørre og meget vinterkolde stepper fra Østrig i nordvest over Lilleasien og Kaukasus til Altajbjergene og Gobiørkenen i sydøst. Arten tåler et højt indhold af salt i jorden. Dens undergrænse for pH i jorden ligger på 6. Derimod er den ikke kræsen med jordtypen og kan tåle oversvømmelse og tilslemning. Den vokser bedst på lysåbne steder med en jord, som er veldrænet og sandet eller leret. Den tåler betydelig tørke, men foretrækker floddale og -bredder, hvor grundvandet står forholdsvist højt. Den tåler temperaturer mellem -45° C og +46° C, og den kan findes fra havniveau og op til 3.438 m højde.[1]
I Centralasien er naboplanterne bl.a. Populus pruinosa og flere andre arter af tørketålende buske og træer, f.eks. Perovskia. Kelkitdalen ligger i Anatolien, og det er ca. 45 km vest for Bayburt, hvor nedslidte skovtyper er udbredt på de nordvendte skråninger. Disse skove er resultatet af, at de oprindelige fyrreskove er forsvundet. Langs floden Kelkit er vegetationen tilpasset den større fugtighed, og her vokser arten sammen med bl.a. almindelig brunelle, almindelig rajgræs, calabrisk fyr, duneg, engriflet hvidtjørn, frynseeg, græsk ene, græsk træranke, hunderose, krimfyr, kyskhedstræ, Rubus canescens (en art af brombær), skarpbladet asparges, skovfyr, strandloppeurt, Tamarix smyrnensis (en art af tamarisk) og Torillis arvensis (en art af randfrø)[2]
Vækstform
Elaeagnus angustifolia - Museum specimen
Smalbladet sølvblad (Elaeagnus angustifolia) er et lille, løvfældende træ eller en stor busk. Nektarmængden er kun lige tilstrækkelig til, at bierne kan overleve at besøge arten. Planten er stærkt salttolerant.
Die Schmalblättrige Ölweide (Elaeagnus angustifolia) ist eine Pflanzenart in der Familie der Ölweidengewächse (Elaeagnaceae).
Die Schmalblättrige Ölweide ist ein sommergrüner, dicht sparrig verzweigter und bedornter Strauch oder kleiner Baum mit meist breiter Krone, der Wuchshöhen von 2 bis 5 Metern, selten bis zu 7 Metern erreicht; in Ausnahmefällen auch höher. Die jungen Zweige und Knospen sind dicht mit silbrigen Schildhaaren besetzt, die wie ein silbriger, abwischbarer Überzug wirken. Die Zweige und Äste besitzen eine dünne rötlich-braune Rinde und verdornte Kurzsprosse.
Die wechselständig angeordneten Laubblätter sind in Blattstiel und Blattspreite gegliedert. Die einfache, ledrige Blattspreite ist bei einer Länge von 4 bis 8 Zentimetern schmal-lanzettlich mit keilförmiger Spreitenbasis und spitzem oder stumpf gerundetem oberen Ende. Die Blattoberseite ist graugrün sowie kahl und die -unterseite silbergrau sowie dicht mit weißlichen Sternhaaren (Trichome) besetzt.
Die Blütezeit reicht von Mai bis Juli. Die kurz gestielten Blüten stehen einzeln oder zu jeweils zwei bis vier in den Blattachseln im unteren Bereich der Zweige. Die zwittrigen oder rein männlichen Blüten haben einen Durchmesser von bis zu 1 Zentimeter und sind vierzählig. Die vier Kelchblätter sind innen hellgelb, außen silbrig behaart und duften angenehm nach Leder. Kronblätter fehlen.
Die hellgelben Früchte sind bei einer Länge von 1 bis 2 Zentimetern ovale bis zylindrische Scheinbeeren. Diese sind geschmacklich sehr aromatisch und essbar. Die Fruchtreife beginnt ab Juli. In Mitteleuropa werden allerdings eher selten Früchte gebildet.
Die Chromosomenzahl beträgt 2n = 28.[1]
Die Schmalblättrige Ölweide lebt in Symbiose (der sogenannten Aktinorrhiza) mit Luftstickstoff bindenden Frankia-Bakterien.[2][3]
Die Bestäubung erfolgt meist durch Bienen. Nach der Anthese stirbt der obere Teil der Kelchröhre ab, der untere Teil umgibt den heranwachsenden Fruchtknoten. Die inneren Teile der Kronröhre werden steinhart, die äußeren mehlig-fleischig, so dass die Frucht einer Steinfrucht ähnelt.
Die Schmalblättrige Ölweide ist im zentralen Asien heimisch. Sie wurde im 17. Jahrhundert in den Mittelmeerraum eingeführt und ist dort weit verbreitet. In Mitteleuropa wird die Schmalblättrige Ölweide oft als Ziergehölz kultiviert und ist stellenweise verwildert.
Elaeagnus angustifolia wurde um 1800 in Nordamerika eingeführt und verwilderte stellenweise, wodurch wie in Europa diese Art auch dort als Neophyt gilt.
Häufige Standorte sind Ufergehölze an Seen und Flüssen, Waldsäume, Gebüsche in sonniger Lage auf lockeren, etwas feuchten Böden.
Die Schmalblättrige Ölweide erträgt formenden Schnitt und bildet dann sehr dichte Hecken. Sie eignet sich so hervorragend als Windschutz. Ebenso wird sie zur Böschungsbefestigung und -begrünung sowie als Rutschhemmer auf Sanddünen gepflanzt. Sie gilt nicht nur als wenig empfindlich gegenüber Luftverunreinigung, sondern erträgt auch recht hohe Konzentrationen von Salzen aller Art im Boden. Insbesondere ist sie gegen Streusalz widerstandsfähig. Allerdings verträgt sie keine strengen Fröste, besonders nicht im späten Frühling.
Für Bienen und andere Hautflügler sind die Blüten eine ergiebige Tracht.
Im Orient werden die getrockneten, nussartig schmeckenden Früchte als Nahrungsmittel verzehrt. Bei Kultursorten sind die Früchte 2 Zentimeter lang und 1 Zentimeter dick. Sie enthalten 10–55 % Eiweiß und sind reich an Glucose, Fructose, Kalium und Phosphor.
Eine experimentelle klinische Studie hat gezeigt, dass Symptome von Osteoarthritis durch die Gabe von E. angustifolia-Extrakt im vergleichbaren Ausmaß gesenkt werden können, wie mit einer Standardtherapie[4].
Die Duftstoffe der Blüten werden in der Parfümindustrie genutzt.
Der bernsteinfarbene Honig ist sehr aromatisch.
Für die Schmalblättrige Ölweide bestehen bzw. bestanden auch die weiteren deutschsprachigen Trivialnamen: böhmischer Ölbaum (Schlesien), Ölbaum (Schlesien), Olivenzeidel, Paradiesbaum und Rächä Weyd (Siebenbürgen).[5]
Die Früchte werden auch als Mehlbeere bezeichnet; als Dekoration für das persische Neujahrsfest Nouruz gehören sie als „Senjed“ zu den sieben Bestandteilen der traditionellen Neujahrstafel Haft Sin.[6]
Die Schmalblättrige Ölweide (Elaeagnus angustifolia) ist eine Pflanzenart in der Familie der Ölweidengewächse (Elaeagnaceae).
Elaeagnus angustifolia, commonly called Russian olive,[1] silver berry,[2] oleaster,[2] or wild olive,[2] is a species of Elaeagnus, native to western and central Asia, Iran, from southern Russia and Kazakhstan to Turkey, parts of Pakistan and parts of India.[3] As of 2020, it is widely established in North America as an introduced species.[4][5]
Elaeagnus angustifolia is a thorny tree growing to 35 feet (11 metres) in height.[6] Its stems, buds, and leaves have a dense covering of silvery to rusty scales. The leaves are alternate, lanceolate, 4–9 centimetres (1+1⁄2–3+1⁄2 inches) long and 1–2.5 cm (3⁄8–1 in) broad, with a smooth margin. The plants begin to flower and fruit from 3 years old. The highly aromatic flowers, produced in clusters of one to three, are 1 cm long with a four-lobed creamy yellow calyx; they appear in early summer and are followed by clusters of fruit, a small cherry-like drupe 1–1.7 cm (3⁄8–5⁄8 in) long, orange-red covered in silvery scales. The fruits are about 1 cm wide[7] and sweet, though with a dryish, mealy texture.[8][9][10]
The species is established and reproduced primarily by seed, with some vegetative propagation also occurring.[11] The branches have thorns that can be 2–7 cm (3⁄4–2+3⁄4 in) long.
Foliage
Microscopic view of leaf scales, which give them a silvery sheen
Fruit
The species was described as Zizyphus cappadocica by John Gerard, and was grown by John Parkinson by 1633.[12] Its common name comes from its similarity in appearance to the olive (Olea europaea), in a different botanical family, the Oleaceae.
The shrub can fix nitrogen in its roots,[13] enabling it to grow on bare mineral substrates.
The caterpillars of the high altitude alpine moth Lachana alpherakii use it as a host plant.[14] The fruit is readily eaten and the seeds disseminated by many species of birds.
The species was introduced into North America by the late 19th century, and was both planted and spread through the consumption of its fruits (which seldom ripen in England),[15] by birds, which disperse the seeds.[11] Russian olive is considered to be an invasive species in many places in the United States because it thrives on poor soil, has high seedling survival rates, matures in a few years, and out-competes the native vegetation. It often invades riparian habitats where the canopy of cottonwood trees has died. Its quick-spreading root system can make it pest-like.
It is widely grown across southern and central Europe as a drought and cold-resistant ornamental plant for its scented flowers, edible fruit,[7] attractive yellow foliage and black bark.[11]
In Iran, the dried powder of the fruit is used mixed with milk for rheumatoid arthritis and joint pains. There is evidence supporting beneficial effects of aqueous extract of Persian olive in reducing the symptoms of osteoarthritis with an efficacy comparable to that of acetaminophen and ibuprofen.[16]
It is one of the seven items used in Haft-sin, a traditional table setting of Nowruz, the traditional Persian spring celebration. The dried fruit, known locally as senjed, is one of seven served in its own syrup in a fruit salad called haft mēwa eaten during Nowruz in Afghanistan.[17][18]
Elaeagnus angustifolia, commonly called Russian olive, silver berry, oleaster, or wild olive, is a species of Elaeagnus, native to western and central Asia, Iran, from southern Russia and Kazakhstan to Turkey, parts of Pakistan and parts of India. As of 2020, it is widely established in North America as an introduced species.
Elaeagnus angustifolia llamado popularmente cinamomo, pangí, árbol del paraíso, olivo de Bohemia y olivillo, es un arbusto o un árbol de hoja caduca de la familia Elaeagnaceae, originario de zonas secas a áridas de Asia Central y Suroccidental de hasta 25 metros de altura con frutos pequeños que recuerdan a los dátiles, pero de escaso valor comercial.
Su nombre común proviene de su similitud en apariencia con el olivo (Olea europaea), de una familia botánica diferente, las oleáceas. No debe confundirse con la misma designación de "árbol del paraíso" con la que se conoce en Argentina, Paraguay y Uruguay a la especie Melia azedarach.[1]
Elaeagnus angustifolia es un árbol que no suele superar los 10 m de altura con la copa redondeada o alargada más o menos irregular, aunque algunos ejemplares alcanzan los 25 metros de altura. Muchos ejemplares tienen el tronco muy inclinado, por lo cual al llegar a cierto tamaño no es infrecuente que se caiga, creando brotes nuevos. Tiene raíces poco profundas y se extienden cerca de la superficie.
El tallo es algo tortuoso con corteza marrón oscuro que se va agrietando y resquebrajando con la edad. Las ramas son espinosas, con ramillas lustrosas de color rojizo. Las hojas son lanceoladas, verde-grisáceas por el haz y plateado-escamosas por el envés. Las flores salen a fines de primavera, formando pedúnculos en las axilas de las hojas, de color blanquecino tirando a amarillo limón por su parte interior. Aparecen solitarias o en conjuntos de dos o tres y desprenden un olor agradable. El fruto es una drupa de aproximadamente 1 cm de largo, ovalada u ovoide-esférica (similares a una pequeña aceituna), de color rojizo-amarillento con un pericarpio comestible de color blanco plateado dulzón y harinoso. La maduración de la fruta comienza en julio en el hemisferio norte en Europa central, sin embargo, rara vez se producen frutas.
La especie puede prosperar en terrenos salinos con la suficiente humedad, por lo cual es frecuente cerca del mar y en cuencas endorreicas salinas.
Es originario de Asia occidental y central, desde el sur de Rusia y Kazajistán e Irán hasta Turquía.
Una de las poblaciones más singulares es la presente en el término municipal de Valdemoro, en el parque denominado "Bolitas del Airón", al ser el único bosquete espontáneo de la península ibérica.[cita requerida]
Crece como árbol invasivo en las márgenes del Río Negro en la Argentina, desde la isla de Choele Choel hasta la ciudad de Viedma.
La madera es considerada de mala calidad y sin valor comercial.
Empezó a cultivarse en 1736, en Alemania. Actualmente, su cultivo está muy extendido en Europa central y meridional, por su uso ornamental y también por sus flores fragantes y su fruto comestible.
Su frutos (aceitunas de Bohemia), son similares en apariencia al fruto del olivo, se consumen frescos, curadas, o molidos en harina, la cual se añade al pan, sopas y otros platos; e igualmente son utilizados para hacer vino con un peculiar aroma especiado. Las frutas se pueden almacenar durante mucho tiempo sin procesar.
Esta especie tolera la poda modeladora y luego forma setos muy densos. Es tan ideal como cortavientos. También se planta para refuerzo de terraplenes y reverdecimiento y como inhibidor de deslizamiento en dunas de arena. No solo se considera menos sensible a la contaminación del aire, sino que también tolera concentraciones bastante altas de sales de todo tipo en el suelo. En particular, es resistente a la sal de la carretera. Sin embargo, no tolera heladas severas, especialmente a finales de primavera.
Su nombre común, "árbol del paraíso", muy probablemente se debe a ser citado en la Biblia como un árbol que se encontraba en el Edén. También se conoce como "olivo de Bohemia" dado el parecido que tienen sus hojas a las del olivo y a ser abundante en esa región. En Andalucía se le conoce como "cinamomo" por su parecido con otro árbol de ese nombre; y también como "pangí".[2]
Respecto al nombre científico, parece ser que Carlos Linneo lo eligió basándose en las palabras griegas "eleia" (olivo) y "agnos" (agnocasto, una planta que se parece al árbol). Otras fuentes aseguran que el nombre deriva de la misma palabra griega "eleia" y la también griega "gennao" (engendrar algo semejante), indicando de este modo su parecido al olivo. Por este mismo parecido es que se lo denomina "olivillo" en la patagonia argentina donde es una especie invasiva en las costas del valle medio del río Negro.
Elaeagnus angustifolia fue descrita por Carlos Linneo y publicado en Species Plantarum 1: 121. 1753.[3]
Elaeagnus angustifolia llamado popularmente cinamomo, pangí, árbol del paraíso, olivo de Bohemia y olivillo, es un arbusto o un árbol de hoja caduca de la familia Elaeagnaceae, originario de zonas secas a áridas de Asia Central y Suroccidental de hasta 25 metros de altura con frutos pequeños que recuerdan a los dátiles, pero de escaso valor comercial.
Idänhopeapensas (Elaeagnus angustifolia) on Euraasiasta kotoisin oleva monivuotinen, kesävihanta, piikikäs pensas, joka kuuluu hopeapensaiden sukuun ja hopeapensaskasvien heimoon.[1]
Idänhopeapensas on epäsäännöllisen pallon muotoinen iso pensas tai pieni puu, jolla on monihaarainen runko, riippuvat oksat sekä pyöreä ja avoin latvus. Se on nuorena nopeakasvuinen ja kasvaa enintään 12 metriä korkeaksi. Nuorilla yksilöillä on harmaa, sileä kaarna ja hopeanhohtoiset, hilseilevät, piikikkäät oksat. Kasvin ikääntyessä kasvu hidastuu ja kaarna muuttuu epätasaiseksi ja ryppyiseksi ja oksat kiiltäviksi ja vaaleanruskeiksi.[1][2]
Idänhopeapensaan silmut ovat melko pienet, pyöreät, hopeisenruskeat ja suomujen peittämät. Lehdet ovat varrella kierteisesti, ja niissä on ehyt lehtilapa, joka on 2–8 senttimetriä pitkä, sentin leveä ja soikean tai suikean muotoinen. Lehden pinta on hilseilevät ja väriltään sameanvihreä tai harmaa ja alapuolelta hopeanhohtoinen.[1]
Idänhopeapensas kukkii tuoksuvin, keltaisin kukin touko–kesäkuussa ja kantaa hedelmää elo–lokakuussa. Sen hedelmät ovat reilun sentin mittaisia marjoja, jotka ovat raakana keltaisia ja kypsänä punaisia ja pysyvät pensaassa pitkälle talveen. Ne kelpaavat myös ihmisravinnoksi ja ovat maultaan makeita ja koostumukseltaan kuivia ja jauhoisia. Kukkiensa ja hopeanharmaiden, pajumaisten lehtiensä vuoksi idänhopeapensas sekoitetaan herkästi hopeapäärynään.[1]
Idänhopeapensaan luontaiseen levinneisyysalueeseen kuuluvat Aasian lauhkeat länsiosat (Afganistan, Armenia, Azerbaidžan, Kiina, Georgia, Iran, Kazakstan, Mongolia, Venäjä, Tadžikistan, Turkmenistan ja Uzbekistan), Aasian tietyt trooppiset alueet (Luoteis-Intia ja Koillis-Pakistan) sekä Kaakkois-Eurooppa (Valko-Venäjä ja Moldova). Se vietiin koristekasviksi 1800-luvun lopussa myös Yhdysvaltoihin, missä se on karannut luontoon ja yleistynyt haitalliseksi asti.[1]
Idänhopeapensas viihtyy etenkin jokien ja purojen rannoilla mutta kasvaa myös tulvatasangoilla, soilla sekä pelloilla ja muilla aukeilla alueilla. Se on vaatimaton lämpötilan, valon määrän ja maaperän suhteen ja sietää hyvin suolaa ja kuivuutta. Se pystyy sitomaan typpeä juuriinsa, minkä ansiosta se selviää hyvin karussa ympäristössä ja syrjäyttää usein muuta rantakasvillisuutta. Idänhopeapensaan marjoja syövät linnut ja muut pieneliöt levittävät sen siemeniä tehokkaasti. Siemenet kestävät hyvin eläinten ruoansulatusnesteitä ja säilyvät itämiskykyisinä jopa kolme vuotta.[1]
Idänhopeapensasta on viljelty jo pitkään koriste- ja aitakasvina, sillä sen tiheä lehvästö on kauniin hopeanhohtoinen ja antaa hyvän näkösuojan. Sitä on käytetty myös hunajakasvina ja mehujen valmistuksessa sekä eroosion estämisessä ja ympäristörakentamisessa. Monet linnut ja nisäkkäät syövät sen marjoja ja pesivät sen oksilla.[1]
Idänhopeapensas (Elaeagnus angustifolia) on Euraasiasta kotoisin oleva monivuotinen, kesävihanta, piikikäs pensas, joka kuuluu hopeapensaiden sukuun ja hopeapensaskasvien heimoon.
Olivier de Bohême, Chalef à feuilles étroites, arbre d’argent, arbre du paradis, olinet, éléagne à feuilles étroites
Elaeagnus angustifolia (olivier de Bohême, arbre d’argent, arbre du paradis, olinet, éléagne à feuilles étroites, chalef à feuilles étroites[1]) est une espèce d'arbuste de la famille des Elaeagnaceae, largement répandu en Asie centrale et de l'ouest, au sud de la Russie, au Kazakhstan, en Turquie et en Iran. Ses fleurs parfumées, ses fruits comestibles et son aspect argenté lui ont valu d'être cultivé ailleurs dans le monde, mais cet Elaeagnus est devenu envahissant dans certains pays.
C'est un arbuste ou arbrisseau à croissance rapide, qui atteint environ 7 mètres de hauteur, en fait de 2 ou 3 m jusqu'à 10 à 12 m[2],[3],[4],[5].
Sa racine pivotante présente un système de racines latérales bien développées. Les rameaux sont couverts, lorsqu'ils sont jeunes, d’écailles argentées ou rousses. Par la suite, les écailles tombent progressivement et les rameaux deviennent brun-rouge luisant. En vieillissant, l'écorce devient grise et striée. Branches et rameaux portent souvent des épines acérées qui mesurent de 0,7 à 3 cm de long[2].
Les feuilles, vert terne lorsqu'elles sont jeunes, se couvrent d’écailles et ont une couleur pouvant aller de l'argenté au rouge-rouille, généralement plus argentée sur la face inférieure qui est plus riche en écailles. À maturité, les écailles tombent et les feuilles deviennent d’un vert plus soutenu. Elles sont portées par un pétiole court (8 mm)[2] et ont une disposition alterne. Elles sont entières, simples, de forme lancéolée à ovale. Elles mesurent de 4 à 8 cm de long et de 1 à 2,5 cm de large[3],[6].
Les fleurs mellifères, à odeur sucrée[7], apparaissent à la fin du printemps ou au début de l'été, soit de mai à juin ou juillet sur son aire de répartition naturelle[2],[3],[5],[6]. Elles apparaissent au niveau de l’aisselle des feuilles, isolées ou par grappes de 2 ou 3. Ces fleurs ont une symétrie radiale et sont portées par un pédicelle court d’environ 2 mm de long[2].
Dans l'ensemble, la fleur mesurent environ 1 cm de long[2],[3],[6]. La corolle est absente[3],[6], ce sont les sépales qui font office de pétales. Les quatre sépales sont partiellement soudés en cloche ou en entonnoir dont la base (= hypanthe) est renflée, charnue, et englobe l'ovaire. La partie soudée des sépales représente un peu moins de 50 % du calice et mesure 5 ou 6 mm de long pour 2,5 à 5 mm de large[2]. La 2e moitié des sépales forme 4 lobes libres, grossièrement triangulaires, avec une ouverture de 5 à 10 mm[3]. L'extérieur de ce calice est blanc argenté, parfois tirant vers le crème argenté, car il est recouvert d’écailles ; il présente parfois à maturité quelques minuscules glandes jaunâtres. L'intérieur du calice est d'un jaune franc, avec parfois quelques glandes brunâtres.
Les quatre étamines, à anthères oblongs, dépassent à peine du calice[3]. Le pistil ne possède qu'un seul carpelle et un seul style. Ce dernier est légèrement courbe, dépasse à peine du calice, et porte un stigmate légèrement déporté sur le côté du style situé vers l'extérieur. L'ovaire est supère, mais enclos dans l'hypanthe, ce qui donne l'impression qu'il est infère.
La pollinisation est entomogame ; les insectes sont attirés par l'odeur de miel des fleurs et par leur production de nectar.
Les fruits apparaissent à la fin de l'été ou à l'automne (d'août à octobre dans l'aire de répartition naturelle de l’espèce)[2]. Bien qu'ayant l'apparence d’une drupe ou d'une baie, ces fruits sont en réalité composés d’un akène englobé dans l'hypanthe devenu charnu[3]. Ils ont la forme d'une petite olive ou d’une petite datte, couverte d'écailles argentées qui deviennent moins nombreuses tandis que la maturité augmente. Sous les écailles, la peau du fruit devient jaune-orangé ou orange, tirant souvent vers le brun-rouge à maturité. Ces fruits mesurent de 0,7 à 2,5 cm de long pour 0,5 à 1,3 cm de large[3],[2]. Le fruit est comestible et sucré, mais avec une texture farineuse[5],[2]. La « graine », qui est en vérité le vrai fruit, est un akène à forme oblongue, qui ne contient qu'une seule graine. Le poids de 1000 graines est d’environ 88 g (5160 graines par livre[4]). Les graines sont généralement disséminées par les animaux qui mangent l'hypanthe charnu et rejettent l'akène plus loin, par exemple les oiseaux qui avalent le fruit et rejettent l'akène dans leurs excréments[6],[8]. Il est envisageable de penser que la dissémination peut aussi se faire grâce à l'eau, car le fruit flotte[8].
Cette espèce présente 2n=28 chromosomes[2].
Écorce d'un vieux tronc
Rameau et feuillage
Détail des fleurs
Coupe d’une fleur ; on voit l'hypanthe encore juvénile à la base du tube floral
Fruit encore vert
Fruits mûrs
Coupe montrant l'akène englobé dans l'hypanthe charnu
Elaeagnus angustifolia - Muséum de Toulouse
Elaeagnus ×ebbingei (ou Elaeagnus ×submacrophylla) est un hybride pouvant être confondu avec Elaeagnus angustifolia. Elaeagnus ×ebbingei est très largement cultivé dans le monde, notamment comme plante de haies, et peut parfois pousser de façon subspontanée. Mais cette espèce a des fleurs crème, sans jaune franc à l'intérieur, qui de plus apparaissent à la fin de l'été et à l'automne, et non à la fin du printemps et en été. De plus, ses feuilles sont nettement plus larges (voir photo ci-contre).
Elaeagnus x caspica, notamment la variété Quicksilver. C'est un hybride spontané et stérile entre Elaeagnus angustifolia et Elaeagnus commutata.
Elaeagnus angustifolia est originaire de l'Asie tempérée et tropicale (de la Chine et la Mongolie jusqu'aux frontières de l'Europe au nord et jusqu'en Iran et Turquie au sud) et de l'Europe de l'Est (Russie, Biélorussie et Moldavie). Elle est cultivée dans de nombreuses autres régions du monde et s'est naturalisée dans certaines, telle que l'Amérique du Nord[2] ou le pourtour méditerranéen[6],[5].
Elle pousse à des altitudes généralement inférieures à 2 000 m[3]. On la trouve souvent près de l'eau : côtes maritimes, rives de lacs et rivières, bordures de fossés, marais, plaines inondables, mais aussi dans le lit de rivières asséchées.
Elle présente une bonne résistance au froid, supportant des températures minimales jusqu'à près de −40 °C[4], mais craint les gelées printanières tardives. c'est plutôt une plante héliophile, n'aimant guère l'ombrage, même si les pousses sont plus tolérantes dans ce domaine que les adultes[4]. Elle supporte une certaine aridité, mais pousse généralement dans des zones où les précipitations annuelles vont de 30 à 100 cm/an[4]. Elle préfère les sols à texture moyenne ou grossière à ceux à texture fine, et sa fourchette de pH optimal est entre 6 et 9,5[4]. Elle tolère la présence de calcaire (CaCO3) ou une salinité modérée[4], mais n'apprécie pas les sols anoxiques[4]. Sa résistance aux incendies est très faible[4].
Elaeagnus angustifolia est une des espèces actinorhiziennes du genre Elaeagnus[9]. Des bactéries du genre Frankia vivant dans les nodules racinaires de l'Olivier de Bohème sont responsables de la fixation de l'azote de l'air[10]. Cette symbiose lui permet de grandir sur des supports minéraux nus[réf. nécessaire].
Ses fleurs parfumées sont mellifères et attirent abeilles et autres insectes pollinisateurs.
L'olivier de Bohême est considéré aux États-Unis comme une espèce envahissante. Sa tendance à s'adapter (voir « Répartition et habitat ») s'accompagne d'une bonne capacité reproductive : même si un fruit ne contient qu'une seule graine (voir « Description »), l'espèce est fructifère (un individu peut produire de nombreux fruits) et la durée de vie des individus est longue[4]. Un individu abimé peut aussi produire des rejets et repousses ; mais cette espèce n'a pas tendance à se reproduire par multiplication asexuée, l'extension de l’espèce se fait essentiellement par le biais des graines[4]. Dans certaines zones, telles que la Camargue ou le bord des étangs du Languedoc, on l'accuse de participer activement à la fermeture de milieux ouverts fragiles tels que les dunes et arrière-dunes, les prés salés ou les prairies humides, ainsi que d'avoir une tendance à évincer ou modifier la flore et la faune locale[5].
Cet Elaeagnus est sensible à certains champignons vivant dans le sol (Verticillium albo-atrum, Verticillium dahliae) responsables de la verticilliose, maladie qui atteint aussi de nombreuses autres espèces[11].
Il est aussi sensible à divers champignons pathogènes provoquant des chancres, tels que Lasiodiplodia theobromae (=Botryodiplodia theobromae), Tubercularia ulmea et Nectria cinnabarina (=Tubercularia vulgaris), ainsi que Phomopsis arnoldiae[12].
Son nom commun « olivier de Bohême » vient de la ressemblance de ses fruits avec l'olivier, mais ces derniers sont des arbres d'une famille distincte (Oleaceae) ; quant à la Bohême, c'est une région de la République tchèque (cette espèce est native en l'Europe de l’Est) : les Anglais nomment cet Elaeagnus Russian olive[2], pour les mêmes raisons, mais aussi Trebizond date[2] (« datte de Trébizonde »), car le fruit peut aussi ressembler à une petite datte, Trébizonde étant l'ancien nom de Trabzon, en Turquie, où l'espèce est native. Le nom « arbre d’argent » est dû aux écailles argentées qui couvrent les jeunes rameaux, les feuilles, l'extérieur des fleurs et les fruits.
Cette espèce a été décrite en 1753 par Carl von Linné dans son ouvrage Species plantarum[13].
D'abord cultivé en Allemagne en 1736[réf. nécessaire], l'arbuste est maintenant largement cultivé en Europe méridionale et centrale en tant que plante ornementale : pour ses fleurs parfumées, ses fruits comestibles, son feuillage argenté attrayant et son écorce sombre. Il a été introduit en Amérique du Nord à la fin du XIXe siècle[réf. nécessaire].
Cette espèce a été officiellement déclarée comme plante invasive dans trois États des États-Unis (Colorado[16], Connecticut[17], Nouveau-Mexique[18]).
Olivier de Bohême, Chalef à feuilles étroites, arbre d’argent, arbre du paradis, olinet, éléagne à feuilles étroites
Elaeagnus angustifolia (olivier de Bohême, arbre d’argent, arbre du paradis, olinet, éléagne à feuilles étroites, chalef à feuilles étroites) est une espèce d'arbuste de la famille des Elaeagnaceae, largement répandu en Asie centrale et de l'ouest, au sud de la Russie, au Kazakhstan, en Turquie et en Iran. Ses fleurs parfumées, ses fruits comestibles et son aspect argenté lui ont valu d'être cultivé ailleurs dans le monde, mais cet Elaeagnus est devenu envahissant dans certains pays.
A árbore do paraíso[1][2] (Elaeagnus angustifolia) é un arbusto ou unha árbore caducifolia da familia Eleagnaceae. Nativa do sueste de Europa e Asia Menor, comezou a se cultivar na Europa Occidental no século XVIII e en América do Norte a fins do século XIX.
Esta árbore pode acadar ata 10 m de altura. Ten follas estreitas, lanceoladas e abrancazadas e flores aromáticas. O froito é unha drupa amarela avermellada, semellante ao dátil, que serve de alimento a moitas especies de paxaros.
O nomes comúns de árbore do paraíso ou oliveira do paraíso[Cómpre referencia] débense moi probabelmente a ser citada na Biblia coma unha árbore que se atopaba no Edén. Oliveira, porque as follas aseméllanse ás desta árbore.
Respecto do nome científico, semella que Carl von Linné o escolleu baseándose nas palabras gregas "eleia" (oliveira) e "agnos" (agnocasto ou árbore da castidade, unha planta que se asemella á árbore). Outras fontes aseguran que o nome deriva da mesma palabra grega "eleia" e a tamén grega "gennao" (enxendrar algo semellante), indicando deste xeito á súa semellanza coa oliveira.
É orixinario de zonas secas a aridas de Asia occidental e central, desde o sur de Rusia e Casaquistán até Turquía.
Unha das poboacións máis senlleiras é a presente en Valdemoro, no parque denominado "Bolitas del Airón", por ser o único arboredo espontáneo da Península Ibérica.
A madeira é considerada de má calidade e sen valor comercial.
Empezou a cultivarse en 1736, en Alemaña. Actualmente, o seu cultivo está moi estendido en Europa central e meridional, polo seu uso ornamental e tamén polas súas flores recendentes e o seu froito comestíbel.
Elaeagnus angustifolia foi descrita por Carl von Linné e publicado en Species Plantarum 1: 121. 1753.[3]
A árbore do paraíso (Elaeagnus angustifolia) é un arbusto ou unha árbore caducifolia da familia Eleagnaceae. Nativa do sueste de Europa e Asia Menor, comezou a se cultivar na Europa Occidental no século XVIII e en América do Norte a fins do século XIX.
Uskolisna zlolesina (srebrna vrba, uskolisna dafina, obična dafina, ruska maslina, divlja maslina; lat. Elaeagnus angustifolia) grmolika je medonosna biljka iz roda Elaeagnus i porodice zlolesinovki (Elaeagnaceae). Raste u zapadnoj i središnjoj Aziji od južne Rusije i Kazahstana do Irana, Turske Afganistana. Kod nas se koristi u hortikulturi. U SAD i Meksiku smatra se invazivnom vrstom.
Elaeagnus angustifolia je trnviti grm, ili manje stablo, visine do 7 metara. Listovi su srebrnasti, kopljasti, dugi do 9 cm. Cvjetovi su maleni, jako mirisavi pa se često koristi za pašu pčela. Plodovi su ovalno izduženi, dužine do 1,7 cm, jestivi. [1]
Dietmar Aichele, Renate Aichele, Heinz-Werner Schwegler: Kosmos Naturführer. Welcher Baum ist das? Bäume, Sträucher, Ziergehölze. 24. Aufl., Franckh-Kosmos, Stuttgart 1992, ISBN 3-440-06570-7.
Uskolisna zlolesina (srebrna vrba, uskolisna dafina, obična dafina, ruska maslina, divlja maslina; lat. Elaeagnus angustifolia) grmolika je medonosna biljka iz roda Elaeagnus i porodice zlolesinovki (Elaeagnaceae). Raste u zapadnoj i središnjoj Aziji od južne Rusije i Kazahstana do Irana, Turske Afganistana. Kod nas se koristi u hortikulturi. U SAD i Meksiku smatra se invazivnom vrstom.
Wuski dźiwi wolijowc (Elaeagnus angustifolia) je štom ze swójby rokotnikowych rostlinow (Elaeagnaceae).
Wuski dźiwi wolijowc (Elaeagnus angustifolia) je štom ze swójby rokotnikowych rostlinow (Elaeagnaceae).
L'olivo di Boemia (Elaeagnus angustifolia L.) è un albero della famiglia Elaeagnaceae originario dell'Asia.[1]
Può raggiungere l'altezza di 10 m ed ha chioma espansa; talvolta ha forma arbustiva ed è, per lo più, spinescente. Le foglie, caduche, alterne, semplici, ovali lanceolate, sono argentee soprattutto nella pagina inferiore. I fiori, solitari o riuniti in fascetti di due o tre, sono argentei all'esterno e gialli all'interno, schiudono in maggio-giugno e sono profumati. I frutti ellissoidali, drupacei, lunghi all'incirca 1 cm, sono giallastri o rossastri; la parte carnosa è dovuta all'accrescimento del perianzio ed è di sapore dolciastro. In Elaeagnus angustifolia var. orientalis i frutti sono particolarmente succosi e dolci; i frutti di tutto il genere sono molto ricercati dalla selvaggina. Il legno, poroso e di facile frattura, poco resistente, non ha alcun valore. È uno dei migliori alberetti a foglia argentea che esplica la sua funzione ornamentale nei giardini dove è apprezzato anche per i fiori profumati.
L'olivo di Boemia (Elaeagnus angustifolia L.) è un albero della famiglia Elaeagnaceae originario dell'Asia.
Siauralapis žilakrūmis (lot. Elaeagnus angustifolia) – žilakrūminių (Elaeagnaceae) šeimos augalų rūšis. Kilusi iš vidurio-vakarų Azijos (pietų Rusija, Kazachstanas, Turkija, Iranas), introdukuota Europoje, Šiaurės Amerikoje.
Tai krūmas arba iki 10 m aukščio užaugantis medis dygliuotomis šakomis. Lapai balsvi, lancetiški, 4-9 cm ilgio. Žiedai geltoni, kvapnūs, su 4 vainiklapiais. Vaisius – 1-1,7 cm ilgio oranžiškai raudonas kaulavaisis (valgomas).
Auginamas Lietuvoje, dažnas. Siauralapis žilakrūmis šviesomėgis, nereiklus dirvožemiui, gerai pakelia sausras, užterštą orą[1].
Ūgliai
Žiedai
Vaisiai
Siauralapis žilakrūmis (lot. Elaeagnus angustifolia) – žilakrūminių (Elaeagnaceae) šeimos augalų rūšis. Kilusi iš vidurio-vakarų Azijos (pietų Rusija, Kazachstanas, Turkija, Iranas), introdukuota Europoje, Šiaurės Amerikoje.
Tai krūmas arba iki 10 m aukščio užaugantis medis dygliuotomis šakomis. Lapai balsvi, lancetiški, 4-9 cm ilgio. Žiedai geltoni, kvapnūs, su 4 vainiklapiais. Vaisius – 1-1,7 cm ilgio oranžiškai raudonas kaulavaisis (valgomas).
Auginamas Lietuvoje, dažnas. Siauralapis žilakrūmis šviesomėgis, nereiklus dirvožemiui, gerai pakelia sausras, užterštą orą.
Ūgliai
Žiedai
Vaisiai
Smalsølvbusk (Elaeagnus angustifolia) er en løvfellende busk eller lite tre i sølvbuskfamilien. Den har sølvfargete blad og en frukt som minner om oliven. Arten hører hjemme i Sentral-Asia, men er vanlig dyrket i mange land og finnes ofte forvillet.
Den blir 3–7, mer sjelden 10 m høy og har en dyp pælerot. Barken er rødbrun, og hos eldre trær har den langsgående furer og skaller av i lange striper. Noen busker har skarpe, 0,3–7 cm lange torner, mens andre mangler dem. Unge greiner og begge bladoverflater er tett dekket av sølvfargete stjernehår. Det finnes en varietet, var. virescens, der bladoversiden er grønn og nesten uten stjernehår. Bladstilken er 5–8 mm lang. Bladene sitter spredt og er avlange til linje-lansettformede, helrandede, 4–8 cm lange og 0,4–3,2 cm brede.[1][2]
Blomstene sitter 1–3 sammen i bladhjørnene. De dufter søtt og er sølvhvite på utsiden, gule inni og 8–10 mm lange. Begeret er klokkeformet med 4 fliker. Kronblad mangler, og det er fire pollenbærere. Frukten minner litt om oliven og er gulbrun, 0,7–2,5 cm lang og 0,5–1,3 cm bred. Den er tett dekket med sølvfargete skjoldhår når den er umoden, men blir seinere nesten glatt. Blomstringen skjer i mai–juni, og frukten er moden i august–oktober.[1][3]
Smalsølvbusk er naturlig utbredt i de tørre og halvtørre områdene i Sentral-Asia fra Nord-Kina og Mongolia i øst til Transkaukasia, Tyrkia og Syria i vest. Det hevdes ofte at den også forekommer naturlig i Europa, men der er den bare naturalisert.[1][4][5]
Smalsølvbusk vokser raskt, opptil 1,8 m i året. Den lever i symbiose med aktinobakterier i slekta Frankia. Bakteriene finnes i utvekster på røttene og fikserer nitrogen fra lufta. Buskene starter å produsere frø når de er 3–5 år gamle. Blomstene pollineres av insekter. Frøene spres med fugler og småpattedyr som eter fruktene. Spredning med vann spiller også en rolle, og frøene kan holde seg flytende opptil 36 timer.[2]
I utbredelsesområdet er somrene varme og vintrene kalde eller svært kalde. Smalsølvbusk vokser langs bredden av elver og innsjøer og kan også forekomme i fjell og ørken. Den tåler alkalisk og saltholdig jord. Selv om den hører hjemme i tørre områder er den avhengig av noe fuktighet og vokser sakte dersom grunnvannsspeilet ligger lavere enn 4 m under marka. Arten finnes i rene bestander, eller sammen med tamarisk, poppel eller Haloxylon. Den tåler skygge når den først har etablert seg.[2]
Smalsølvbusk ble brukt til leplanting i vestlige USA. Den har spredt seg mye og opptrer som en invasiv art langs elver i dette området, ofte sammen med invasive tamariskarter. Arten fortrenger naturlig vegetasjon som poppel og pil, og de nitrogenrike bladene tilfører ekstra nitrogen til økosystemet. Smalsølvbusk har hatt fordel av vassdragsreguleringer som fører til mindre flommer slik at kantvegetasjonen ikke skylles bort så ofte. Bever foretrekker poppel og rører nesten ikke smalsølvbusk.[2][6]
Arten er naturalisert i sørlige og østlige deler av Europa, og også her skaper den problemer ved å redusere artsmangfoldet og fortrenge opprinnelige arter. I Ungarn har fjerning av smalsølvbusk i en nasjonalpark ført til at forsvunnede orkidéarter har kommet tilbake. Ved saltsjøer fører arten til reduksjon i antall vannfugler. Skjære bygger ofte reir i smalsølvbusker, og skjæra er en viktig predator på vannfuglenes egg og unger.[4][5]
I mange land er smalsølvbusk mye brukt som hageplante på grunn av de vakre bladene. Den dyrkes både som tornete hekkplante og som enkeltstående trær. Arten blir også brukt i lebelter og for å revegetere områder der grunnen er forurenset av gruvedrift eller industri. Smalsølvbusk tåler vind, næringsfattig jord og salt i luft og jord. I motsetning til slektningen tindved har den ikke plagsomme rotskudd. Smalsølvbusk er lite brukt i Norge, men kan dyrkes til herdighetssone 5, altså i store deler av Sør-Norge.[7][8][2]
Honningbier besøker blomstene for nektaren. Fruktene spises ferske eller tørket. De inneholder proteiner, sukker, vitaminer og mineraler. Frukten blir også brukt til å fremstille gelé og alkoholholdig drikke. Uttrekk av frukt, blomster, løvverk og bark er tradisjonelt brukt mot en rekke sykdommer. Planten skal hjelpe mot blant annet sår hals, hoste, forkjølelse, feber, kvalme, oppkast og diaré. Farmakologiske studier viser at smalsølvblad har antioksiderende, betennelsesdempende, antimutagen og smertestillende virkning.[9][3]
Bark på ungt tre
Bark på eldre tre
Blomster
Blader og umoden frukt
Stjernehår
Frukt
. PMID 28053884. doi:10.1016/j.jtcme.2015.09.004. 
Smalsølvbusk (Elaeagnus angustifolia) er en løvfellende busk eller lite tre i sølvbuskfamilien. Den har sølvfargete blad og en frukt som minner om oliven. Arten hører hjemme i Sentral-Asia, men er vanlig dyrket i mange land og finnes ofte forvillet.
Oliwnik wąskolistny (syn. oliwnik zwyczajny) Elaeagnus angustifolia L. – gatunek rośliny z rodziny oliwnikowatych. Występuje na obszarze od Europy po środkową Azję i Himalaje, ponadto w Chinach[2]. W Polsce jest dość często uprawiany, czasami dziczejący i lokalnie zadomowiony (kenofit)[3].
Jest łatwy w uprawie, nie ma specjalnych wymagań co do gleby. Można go silnie przycinać, wówczas zagęszcza się i ma ładniejszy pokrój. Rozmnaża się go przez wysiew nasion.
Oliwnik wąskolistny (syn. oliwnik zwyczajny) Elaeagnus angustifolia L. – gatunek rośliny z rodziny oliwnikowatych. Występuje na obszarze od Europy po środkową Azję i Himalaje, ponadto w Chinach. W Polsce jest dość często uprawiany, czasami dziczejący i lokalnie zadomowiony (kenofit).
Elaeagnus angustifolia é uma espécie de planta com flor pertencente à família Elaeagnaceae.
A autoridade científica da espécie é L., tendo sido publicada em Species Plantarum 1: 121. 1753.
Os seus nomes comuns são árvore-do-paraíso, oleastro ou oliveira-do-paraíso.[1]
Trata-se de uma espécie presente no território português, nomeadamente no Arquipélago dos Açores e no Arquipélago da Madeira.
Em termos de naturalidade é introduzida nas duas regiões atrás referidas.
Não se encontra protegida por legislação portuguesa ou da Comunidade Europeia.
Elaeagnus angustifolia é uma espécie de planta com flor pertencente à família Elaeagnaceae.
A autoridade científica da espécie é L., tendo sido publicada em Species Plantarum 1: 121. 1753.
Os seus nomes comuns são árvore-do-paraíso, oleastro ou oliveira-do-paraíso.
Salcia mirositoare, sau sălcioară, (Elaeagnus angustifolia L.), este un arbore ornamental de mici dimensiuni (înălțimi de până la 5–6 m), întâlnit uneori prin parcuri. Frunzele sunt simple, cu marginea întreagă, argintii, dispuse altern. Florile sunt mici, alb-tomentoase, cu miros plăcut. Fructele sunt sferice sau ovale, deschise la culoare, cu un înveliș cărnos, persistente peste iarnă. Sălcioara rezistă bine la secetă și se dezvoltă bine și în condițiile unor soluri mai sărace în substanțe nutritive.
Frunzele și lujerii argintii tomentoși, precum și florile plăcut mirositoare, oferă o valoare ornamentală destul de ridicată acestei specii.
Sălcioara este utilizată îndeosebi ca specie ornamentală, dar poate prezenta importanță și din punct de vedere apicol sau pentru ameliorarea proprietăților solului.
Materiale media legate de Sălcioară la Wikimedia Commons
Salcia mirositoare, sau sălcioară, (Elaeagnus angustifolia L.), este un arbore ornamental de mici dimensiuni (înălțimi de până la 5–6 m), întâlnit uneori prin parcuri. Frunzele sunt simple, cu marginea întreagă, argintii, dispuse altern. Florile sunt mici, alb-tomentoase, cu miros plăcut. Fructele sunt sferice sau ovale, deschise la culoare, cu un înveliș cărnos, persistente peste iarnă. Sălcioara rezistă bine la secetă și se dezvoltă bine și în condițiile unor soluri mai sărace în substanțe nutritive.
Frunzele și lujerii argintii tomentoși, precum și florile plăcut mirositoare, oferă o valoare ornamentală destul de ridicată acestei specii.
Kuş iğdesi (Elaeagnus angustifolia), iğdegiller (Elaeagnaceae) familyasından kışın yaprağını döken çoğunlukla çalı, bazen 7–8 m'ye kadar boylanabilen bir iğde türü.
Sürgünleri dikenli olan bitkinin, söğüt yapraklarına benzeyen kısa saplı ve dar şerit biçimindeki yaprakları vardır. 4–8 cm uzunluğundaki yaprakların üst yüzü mat-yeşil alt yüzü gümüşi renktedir. Çiçekler 1-3'lü kısa salkımlar halinde gümüşi renkte ve güzel kokuludur. Meyvesi, portakal sarısı ya da kendine has bir renktedir. Meyvesi yenmemekte ancak kabuğunun altında bulunan unlu tatlı kısmı yenmektedir.
Kuş iğdesi; Rusya ve Kazakistan'ın güneyinden Türkiye ve İran'ı da içine alan Batı ve Orta Asya Batı ve Orta Asya'da yerli tür olarak yetişmektedir. 17. yüzyılda yapılan kültür çalışmalarıyla Avrupa'da da görülmeye başlayan bu tür, insan faaliyetleri sonucu 19. yüzyıldan itibaren Kuzey Amerika kıtasında da görülmeye başlamıştır. Türkiye'nin Orta Anadolu Bölgesi ağırlıklı olmak üzere hemen her yerinde yetişmektedir.
Kuş iğdesi (Elaeagnus angustifolia), iğdegiller (Elaeagnaceae) familyasından kışın yaprağını döken çoğunlukla çalı, bazen 7–8 m'ye kadar boylanabilen bir iğde türü.
Кущ або невеличке дерево заввишки 3-8 м з розлогою, часто асиметричною, кроною. Стовбур вкритий коричнево-сірою розтрісканою корою, тонкі гілки коричневі, гладкі, з поодинокими колючками, наймолодші пагони сріблясто-сірі від зірчастих волосків. Листки чергові, черешкові, дуже мінливі за формою (від лінійних до видовжено-ланцетних), зверху зеленкувато-сріблясті, зісподу — біло-сріблясті, завдовжки 2,5-9 см, завширшки 0,4-2,5 см. Черешки завдовжки 5-11 мм. Листкові пластинки при основі ширококлиноподібні, при верхівці — загострені, цілокраї.
Квітки двостатеві, дуже запашні, зібрані по 1-3 штуки у пазухах листків, розташовані на коротких (1,5-4 мм) квітконіжках. Пуп'янки булавчастої форми. Оцвітина актиноморфна, чотирилопатева, тубчасто-дзвоникувата, ззовні сріблясто-біла від зірчастих волосків, всередині яскраво-жовта (на початку цвітіння) або блідо-жовта (наприкінці цвітіння), завдовжки 3-4 мм, завширшки 6-10 мм. Відгин пелюсток трикутно-загострений. Тичинок чотири, вони дуже короткі, прикріплені до зіва оцвітини і чергуються з її частками. Пиляки довгасті, жовті. Маточка одна, зав'язь верхня, стовпчик один, у верхній частині він дещо зігнутий. Плід — округло-яйцеподібна, жовта кістянка завдовжки 0,7-2 см. Кісточка з вісьмома борозенками.
Число хромосом 2n = 28.
Загалом за багатьма морфологічними ознаками (форма і колір листя, вигляд квіток і плодів) маслинка вузьколиста дуже схожа на європейську маслину, хоча ці дерева систематично не споріднені.
Ареал виду охоплює Малу та Середню Азію, Кавказ, південну частину Східної Європи. На сході він сягає Західного Сибіру, Алтайських гір, на півдні — Середземномор'я, на півночі — Центральної Європи, втім в останньому регіоні плодоношення спостерігається рідко. В Україні маслинка вузьколиста зростає по всій території, але частіше трапляється в південних областях.
Крім того, цей вид завезений до США. У південних штатах він натуралізовався, а в штатах Колорадо, Нью-Мексико, Коннектикут навіть оголошений інвазивною рослиною. Висувались припущення, що агресивне поширення маслинки вузьколистої зумовлене алелопатією, втім лабораторні дослідження показали — пригнічуючі властивості опалого листя цього виду посередні.[4]
Рослина світлолюбна, морозостійка (витримує пониження температури до −40 °C), хоча чутлива до пізніх весняних приморозків. Коріння маслинки вузьколистої здатне фіксувати азот за допомогою бактерій Frankia, завдяки чому це дерево може рости навіть на неплідних кам'янистих схилах. Загалом до якості ґрунтів цей вид невибагливий, витримує навіть їх засолення, але погано переносить нестачу кисню.
В природі маслинка вузьколиста тяжіє до джерел води, хоча добре переносить спеку та посуху. На півдні України вона часто росте на пляжах та берегах лиманів. В горах зростає переважно на висотах 700–1300 м над рівнем моря, вище 2000 м не стрічається.
Квітне в кінці травня — на початку червня, загалом цвітіння триває близько 10 діб.[3] Пахощі маслинки вузьколистої солодко-медові і приваблюють багатьох перетинчастокрилих комах, а надто бджіл, які виступають основними запилювачами (вони збирають переважно нектар). Плоди достигають у серпні-вересні, їх охоче поїдають птахи. Насіння не перетравлюється у травній системі пернатих, після випорожнення воно потрапляє на землю і таким чином поширюється. Насіння не тоне у воді, тому додатковим шляхом поширення може бути гідрохорія. Окрім насіннєвого можливе і вегетативне розмноження, хоча в природі воно не відіграє істотної ролі.
В культурах росте в чистих і мішаних насадженнях у суміші з білою акацію, тополями, рідше з широколистяними породами. Культивується в садах, парках, захисних насадженнях, лісосмугах по всій Україні, але найпоширеніша y степу і лісостепу.
Маслинка вузьколиста — гарний ранньолітній медонос, дає підтримуючий взяток і сприяє нарощуванню сили сім'ї бджіл перед літнім головним взятком, особливо в степових районах, де угіддя відзначаються недостатнім весняним запасом нектару. Бджоли здатні зібрати 4-13 кг меду на вулик або від 60 до 200 кг з гектара суцільних насаджень. Кожна квітка продукує 0,35-0,37 мг цукру у нектарі. Мед з маслинки бурштинового кольору, запашний.[3]
Плоди їстівні, на смак солодкі, з борошнистим присмаком. Вони багаті на вуглеводи, серед яких переважають цукри (до 70% у м'якуші), клітковина (понад 6%), крохмаль (1,5%). Також у плодах міститься чимало білку (10-55%), фосфорних і калійних солей, слиз і таніди. Заготовляють їх у районах вирощування. У Середній Азії та на Кавказі, в Криму плоди маслинки їдять свіжими як ласощі, готують різні національні страви. В кондитерській промисловості маслинку можна використовувати для виготовлення цукатів та інших виробів. Борошно з висушених плодів додають до пшеничного під час випікання солодкого хліба, булочок, печива, тістечок. З плодів маслинки виготовляють смачні вина, що мають своєрідний пряний аромат. З м'якоті женуть горілку.[5]
У народній медицині використовують плоди маслинки при хворобах травних органів як в'яжучий і обволікаючий засіб. Квіти використовують при простудних захворюваннях для втирання. У гомеопатії із стиглих плодів виготовляють настойки.
Кора і листки маслинки містять таніди і фарбувальні речовини. Ними можна фарбувати тканини в коричневий і чорний кольори і дубити шкури. На стовбурі маслинки утворюється камедь, яка може знайти застосування в текстильній промисловості для ситцедрукування, вона в певній мірі може замінити імпортну сенегальську камедь і гумітрагант. Ефірна олія з квіток цього дерева використовується у парфумерній та в інших галузях промисловості.
Маслинка вузьколиста має тверду, щільну деревину жовтого кольору, яку використовують для виготовлення столярних і токарних виробів та музичних інструментів. Дрова з маслинки горять погано, даючи неприємний запах.
Маслинка має велике значення у фітомеліоративних і менше у декоративних насадженнях. Вона широко використовується в захисних смугах, у лісових насадженнях (особливо на засолених ґрунтах), для створення живоплотів і закріплення крутосхилів. Разом з тим насадження маслинки вузьколистої на залізорудних відвалах нетривкі і вже у віці 20-25 років такі дерева передчасно всихають.[6]
Nhót lá hẹp (danh pháp khoa học: Elaeagnus angustifolia) là một loài thực vật có hoa trong họ Elaeagnaceae. Loài này được L. mô tả khoa học đầu tiên năm 1753.[1]
Bài viết liên quan đến bộ Hoa hồng này vẫn còn sơ khai. Bạn có thể giúp Wikipedia bằng cách mở rộng nội dung để bài được hoàn chỉnh hơn. Nhót lá hẹp (danh pháp khoa học: Elaeagnus angustifolia) là một loài thực vật có hoa trong họ Elaeagnaceae. Loài này được L. mô tả khoa học đầu tiên năm 1753.
Elaeagnus angustifolia L., 1753
Лох узколи́стный (лат. Elaeágnus angustifólia), или лох восточный[2], или пшат (фесида)[3] (Elaeagnus orientalis) — вид древесных растений рода Лох (Elaeagnus) семейства Лоховые (Elaeagnaceae). Южноевропейско-центральноазиатский вид.
Н. И. Анненков в «Ботаническом словаре» (1878) в статье о лохе приводит следующие простонародные и книжные названия, употреблявшиеся в разных местностях России с указанием лиц, зафиксировавших эти названия в печати или письменно, а также названия на немецком, французском и английском языках:
Elaeagnus hortensis M. a B. a. angustifolia. Іерусалимская верба (Güld.) Цареградская верба (Сред.) Цареградская лоза (Малор. пер.) С е р е б р я н о е д е р е в о (у сад. съ нѣм.) Оливное дерево (Полт. съ нѣм.) Масличное дерево (Малор. съ нѣм.) Джида (Вѣстн. Геогр. Общ.) Маслина (Екат.) Дикая Маслина (а не Малина, какъ у Левш.) Л о х ъ, Л о х о в и н а, Л о х о в н и к ъ. — Кирг. Джиддэ (Борщ.) Джигда (въ Ходж.) Джида (Сарты Афг.) Dchigde. — Бух. Dschidda, Dschigda. Дженгердукъ (Кир.) Перс. Ssandschid, Ssind-shid. — Хив. Джигердакъ (Кир.) — Тат. Игда (Сит. на Кавк.) — Нѣм. Oleaster, der falsche, wilde Oelbaum, der Paradiesbaum, der Silberbaum. — Франц. L’Olivier de Bohème. — Англ. Wild Olive Tree, Jerusalem Willow.
β. inermis. П ш а т ъ (съ арм.) Армянскіе или Бухарскіе, или Кавказскіе, или Китайскіе, или Туркменскіе финики. — Арм. Pschatt. — Груз. Пшати (Эр.) — Турк. Igda (Buhs.) — Перс. Ssedschit (Buhs.) — Плоды иногда наз. Жужубой по смешенію съ плодами Zizyphus. Они съѣдобны и довольно вкусны. Киргизы приготовляютъ изъ нихъ муку и варятъ изъ нихъ родъ компота, который славится у нихъ полезнымъ отъ поноса.[4]
Дико произрастает в Восточной Европе, на Кавказе, в Средней Азии, Малой Азии, Иране. На территории России встречается в европейской части, на Северном Кавказе, в Западной Сибири и Алтайском крае[5].
Весьма засухоустойчив, почти не страдает от жарких суховеев в юго-восточных степных районах. К почвам неприхотлив; переносит значительную засолённость почвы, успешно произрастает на каштаново-солонцовых, тёмно-каштановых и светло-каштановых почвах. При засыпании ствола песком образует обильные придаточные корни. Очень хорошо переносит пыль, копоть, газ.
Хорошо переносит стрижку и потому вполне пригоден для живых изгородей, однако в этом случае нуждается в регулярной обрезке, иначе снизу быстро оголяется и перерастает в деревцо. Цвести и плодоносить начинает с 3—5-летнего возраста.
Кустарник или невысокое дерево высотой 3—7 м, иногда с колючками.
Молодые побеги серебристые, остальные серые.
Листья линейно- или продолговато-ланцетные, ланцетно-овальные или яйцевидные, с черешками, длиной 5—8 см, островершинные, к основанию суженные, сверху серовато-зелёные, снизу серебристо-белые от серебристых чешуек, покрывающих обе стороны листа.
Цветки длиной до 1 см, очень душистые, одиночные, в пазухах листьев; околоцветник серебристо-белый с желтоватыми жилками, внутри жёлтый.
Формула цветка: ∗ K ( 4 ) C 0 A 4 G 1 _ {displaystyle ast K_{(4)};C_{0};A_{4};G_{underline {1}}} 
Плод — костянка длиной около 1 см, овальная или яйцевидно-шаровидная, красновато-желтоватая с серебристо-белым сладковато-мучнистым съедобным околоплодником.
Цветёт в средней полосе в июне, на юге Казахстана и в странах Средней Азии во второй и третьей декадах мая. Плоды созревают в августе—октябре.
Размножается семенами, черенками, отводками, возобновляется также порослью (корневых отпрысков не дает).
В плодах содержится свыше 40 % сахаров, в том числе глюкоза, около 20 % фруктозы, более 10 % белка, соли калия и фосфора, до 40 % свободного и связанного танина, органические кислоты, красящие вещества. В листьях имеется аскорбиновая кислота (0,140—0,35 %), в коре алкалоиды, дубильные и красящие вещества, в цветках — приятно пахнущее эфирное масло (0,3 %).
Растения в возрасте 5—12 лет интенсивно выделяют камедь.
Древесина лоха узколистного жёлтого цвета, кольцесосудистая, широкослойная, с узкой заболонью и желтовато-бурым ядром; плотность при 15 % влажности 670—710 кг/м3, при 12 % — 690 кг/м3. Древесина вязкая, твёрдая, стойкая против гниения, хорошо сохраняется в воде; сушится без коробления и растрескивания; хорошо обрабатывается режущими инструментами, отделывается. Используется на колья, столярные и точёные изделия, музыкальные инструменты, для изготовления мебели[7]. Упоминается в Библии в качестве материала для оформления церкви.
Культивируют в садах[7], парках, высаживают в качестве почвоукрепляющего и водозащитного растения. Серебристые листья, яркая кора, душистые цветки делают лох весьма декоративным растением[7]. Легко переносит стрижку и пересадку, газо- и дымоустойчив в условиях города.
Плоды лоха используют в пищу[7], их едят свежими и размалывают на муку, которую добавляют в хлеб, супы и другие блюда; используют для приготовления вина со своеобразным пряным ароматом. Плоды могут долго сохраняться без переработки.
Лох служит также источником получения вяжущего средства для лечения заболеваний пищеварительного тракта[7]. Это средство было предложено в виде высушенной и размолотой мучнистой части плодов лоха С. А. Мирзояном и названо им пшатином.[источник не указан 2201 день]
Настойку свежих зрелых плодов используют в гомеопатии. В народной медицине цветки употребляли при отёках, цинге, как противоглистное, при колите, бронхите, болезнях сердца; листья — при ревматизме и подагрических болях, а также как ранозаживляющее.
Кору и листья используют для дубления кож[7] и окрашивания их в чёрный и коричневый цвета.
Хороший раннелетний медонос[7], даёт преимущественно нектар. Мёд янтарного цвета с приятным ароматом.
Подсочкой получают камедь[7], употребляемую для изготовления клея, красок и лаков.
Вид Лох узколистный входит в род Лох (Elaeagnus) семейства Лоховые (Elaeagnaceae) порядка Розоцветные (Rosales).
Лох узколи́стный (лат. Elaeágnus angustifólia), или лох восточный, или пшат (фесида) (Elaeagnus orientalis) — вид древесных растений рода Лох (Elaeagnus) семейства Лоховые (Elaeagnaceae). Южноевропейско-центральноазиатский вид.
沙枣（Elaeagnus angustifolia）也称银柳、香柳、桂香柳。用于水土保持、防沙护林。
沙枣为落叶乔木或小灌木，老枝呈栗褐色，一般具有棘刺，幼枝常被银白色的鳞片。
披针形的叶子，两面都有银白色鳞片，背面比较密；夏季开出芳香的银白色小花，1－3朵生于小枝下部叶腋；长椭圆形果实，成熟时为栗褐色，也密被有银白色鳞片。
分布于中国北部地区，地中海沿岸，俄罗斯、印度也有生长。一般生长于沙漠地区，也有栽培。
分類（APG III） 界 : 植物界 Plantae 階級なし : 被子植物 Angiosperms 階級なし : 真正双子葉類 Eudicots 階級なし : コア真正双子葉類 Core eudicots 階級なし : バラ類 Rosids 階級なし : 真正バラ類I Eurosids I 目 : バラ目 Rosales 科 : グミ科 Elaeagnaceae 属 : グミ属 Elaeagnus 種 : ヤナギバグミ E. angustifolia 学名 Elaeagnus angustifolia L. 英名 Silverberryヤナギバグミ（学名：Elaeagnus angustifolia）は被子植物グミ科グミ属に属する植物で、中央アジアの乾燥地帯でよく見られる。沙漠などの乾燥に強く、タマリスクとコトカケヤナギと共に「沙漠の3英雄（植物）」とも呼ばれる。
中国語名称は「砂棗」（さそう、すななつめ）で、隣国・中国新疆ウイグル自治区に多く生育しているので、そこへの旅行経験者も含めて日本でもスナナツメと呼ぶ人もいる。 [1]
この項目は、植物に関連した書きかけの項目です。この項目を加筆・訂正などしてくださる協力者を求めています（プロジェクト:植物／Portal:植物）。 
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