Wildlife, Animals, and Plants
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Introductory
SPECIES: Salix exigua | Sandbar Willow
ABBREVIATION :
SALEXI
SYNONYMS :
Salix argophylla Nutt.
Salix fluviatilis var. exigua (Nutt.) Sarg.
Salix interior Rowlee
Salix interior var. angustissima (Anderss.) Dayton
Salix interior var. exterior Fern.
Salix interior var. pedicellata (Anderss.) Ball
Salix interior var. wheeleri Rowlee
Salix longifolia Muhl. non Lam.
Salix longifolia var. angustissima Anderss.
Salix longifolia var. argophylla (Nutt.) Anderss.
Salix longifolia var. exigua (Nutt.) Bebb
Salix longifolia var. pedicellata Anderss.
Salix stenophylla Rydb.
SCS PLANT CODE :
SAEX
COMMON NAMES :
sandbar willow
sand-bar willow
coyote willow
dusky willow
narrowleaf willow
slender willow
basket willow
acequia willow
gray sandbar willow
silvery desert willow
TAXONOMY :
There has been considerable disagreement over the taxonomy of the Salix
exigua complex. Entities in this complex have been interpreted
variously as distinct species [1,15,16] or as subspecies
[7,10,22,27,62]. However, because the Salix exigua complex has many
forms and freely interbreeding intermediates, ranking entities at the
subspecific level appears to be more correct. The fully documented
scientific name of sandbar willow is Salix exigua Nutt. Recognized
subspecies and varieties [7,10,22,27,62], and a proposed variety [10]
are:
Salix exigua
ssp. exigua
var. exigua
var. stenophylla
ssp. interior
var. pedicellata
var. interior
ssp. melanopsis
var. melanopsis
var. tenerrima (Brunsfeld and Johnson 1985)
LIFE FORM :
Tree
FEDERAL LEGAL STATUS :
No special status
OTHER STATUS :
NO-ENTRY
COMPILED BY AND DATE :
Ronald Uchytil/March 1989
LAST REVISED BY AND DATE :
NO-ENTRY
AUTHORSHIP AND CITATION :
Uchytil, Ronald J. 1989. Salix exigua. In: Remainder of Citation
DISTRIBUTION AND OCCURRENCE
SPECIES: Salix exigua | Sandbar Willow
GENERAL DISTRIBUTION :
Sandbar willow occurs from eastern Quebec and New Brunswick west across
Canada to central Manitoba, Yukon Territory, and central Alaska, south
through British Columbia and Washington to southern California, and
southeast to southern Texas, southern Louisiana, western Tennessee,
Kentucky, and Virginia [8,35]. The ranges of subspecies exigua and
interior overlap. Subspecies exigua is found from British Columbia,
Montana, and the Black Hills south to New Mexico, Arizona, and Texas.
Subspecies interior is found from New Brunswick to Alaska, south to
Maine, Virginia, Kentucky, Lousiana, Arkansas, and New Mexico [22,54].
ECOSYSTEMS :
FRES10 White - red - jack pine
FRES11 Spruce - fir
FRES15 Oak - hickory
FRES17 Elm - ash - cottonwood
FRES18 Maple - beech - birch
FRES19 Aspen - birch
FRES20 Douglas-fir
FRES21 Ponderosa pine
FRES26 Lodgepole pine
FRES28 Western hardwoods
FRES29 Sagebrush
FRES34 Chaparral - mountain shrub
FRES38 Plains grasslands
FRES39 Prairie
STATES :
AK AZ AR CA CO ID KS KY LA ME
MI MN MO MT NE NV NM ND OK OR
SD TN TX UT VA WA WI WY AB BC
MB NB PQ YT MEXICO
ADMINISTRATIVE UNITS :
AGFO APIS ARCH BADL BAND BITH
BICA BLRI BRCA BUFF CACH CANY
CARE CEBR CHCU COLM CODA CRMO
CUVA DEVA DEWA DINO EFMO FLFO
FOBO GATE GLAC GLCA GRCA GRTE
GRKO GRBA INDU JODA LAME LAMR
MACA MEVE NABR PEFO PIRO PIPE
ROMO SAGU SLBE THRO TICA WICA
YELL YOSE YUCH ZION
BLM PHYSIOGRAPHIC REGIONS :
5 Columbia Plateau
6 Upper Basin and Range
7 Lower Basin and Range
8 Northern Rocky Mountains
9 Middle Rocky Mountains
10 Wyoming Basin
11 Southern Rocky Mountains
12 Colorado Plateau
13 Rocky Mountain Piedmont
14 Great Plains
15 Upper Missouri Basin and Broken Lands
KUCHLER PLANT ASSOCIATIONS :
K011 Western ponderosa forest
K012 Douglas-fir forest
K016 Eastern ponderosa forest
K017 Black Hills pine forest
K018 Pine - Douglas-fir forest
K019 Arizona pine forest
K020 Spruce - fir - Douglas-fir forest
K023 Juniper - pinyon woodland
K033 Chaparral
K035 Coastal sagebrush
K037 Mountain-mahogany - oak scrub
K038 Great Basin sagebrush
K039 Blackbrush
K040 Saltbush - greasewood
K041 Creosotebush
K042 Creosotebush - bursage
K049 Tule marshes
K051 Wheatgrass - bluegrass
K055 Sagebrush steppe
K056 Wheatgrass - needlegrass shrubsteppe
K057 Galleta - threeawn shrubsteppe
K063 Foothills prairie
K064 Grama - needlegrass - wheatgrass
K065 Grama - buffalograss
K066 Wheatgrass - needlegrass
K070 Sandsage - bluestem prairie
K075 Nebraska Sandhills prairie
K093 Great Lakes spruce - fir forest
K095 Great Lakes pine forest
K098 Northern floodplain forest
K106 Northern hardwoods
SAF COVER TYPES :
1 Jack pine
5 Balsam fir
16 Aspen
63 Cottonwood
108 Red maple
202 White spruce - paper birch
210 Interior Douglas-fir
217 Aspen
218 Lodgepole pine
222 Black cottonwood - willow
235 Cottonwood - willow
SRM (RANGELAND) COVER TYPES :
NO-ENTRY
HABITAT TYPES AND PLANT COMMUNITIES :
Sandbar willow usually occurs in early seral communities. These are
typically riparian and occur as narrow bands immediately adjacent to the
stream or river edge. Throughout the Rocky Mountain States, it commonly
occurs as a dense shrub layer adjacent to bottomlands of cottonwood
(Populus spp.) and birch (Betula spp.) [23,31,60]. Published
classifications listing sandbar willow as an indicator or dominant in
community types (cts), habitat types (hts), plant associations (pas),
riparian site types (rst), or riparian zone associations (rzas) are
presented below:
Area Classification Authority
sw US riparian hts Szaro & Patton 1987
sw US wetland cts Brown 1979
AZ,NM riparian pas Pase & Layser 1977
c CO: Arapaho & forest hts Hess & Alexander 1986
Roosevelt NFs
CO: Gunnison & forest hts Komarkova & others 1988
Uncompahgre NFs
e CO: South Platte riparian cts Lindauer 1983
& Arkansas
Rivers
e ID,w WY riparian cts Youngblood & others 1985a
ID: Upper & Middle riparian cts Platts & others 1987
Forks Salmon
River
sw MT riparian veg. rst, hts, cts Hansen & others 1988
MT riparian dominance types Hansen & others 1988
sw NM riparian cts Medina 1986
sc OK bottomland cts Petranka & Holland 1980
OR: Deschutes, riparian cts Kovalchik 1987
Ochoco,Fremont
& Winema NFs
n UT,s ID riparian cts Padgett & others 1985
VALUE AND USE
SPECIES: Salix exigua | Sandbar Willow
WOOD PRODUCTS VALUE :
NO-ENTRY
IMPORTANCE TO LIVESTOCK AND WILDLIFE :
Sandbar willow is an important food source for many wildlife species.
In the Great Basin it has been reported as a favorite food of beaver
[41]. Willows (Salix spp.) in general are a preferred food of moose,
and sandbar willow occurs in riparian and flood plain habitats which
these animals frequent [6,30,34,45]. It also is browsed heavily by elk
[45] but is of only slight improtance as browse for mule deer [57].
Dense stands provide hiding cover for wildlife but at the same time
limit access for livestock [23,24]. Stands in eastern Colorado are used
extensively by waterfowl during winter [35].
PALATABILITY :
Van Dersal [57], reported that sandbar willow is relished by livestock.
In the West, willows are generally considered to be more palatable to
sheep than to cattle, but cattle may make greater use of willow plants
because they tend to frequent riparian areas [56]. Most willows are
highly palatable to moose, especially in winter, and make up a high
percentage of their diet on western ranges [45]. The palatablity of
sandbar willow to livestock and wildlife species in several western
states has been rated as follows [14,51,53,29]:
CA CO UT WY
Cattle poor fair fair ----
Sheep fair fair fair ----
Horses poor fair fair ----
Moose ---- ---- ---- good
Mule deer fair ---- good ----
White-tailed deer fair ---- ---- ----
NUTRITIONAL VALUE :
Sandbar willow's energy value is rated as fair and its protein value as
poor [14].
COVER VALUE :
Sandbar willow can form stands or thickets several meters thick, with
densely spaced stems. These stands provide excellent hiding cover for
numerous wildlife species [23]. In California, the endangered Least
Bell's Vireo frequently nests in willow thickets [21].
The degree to which sandbar willow provides environmental protection
during one or more seasons for wildlife species has been rated as
follows [14,18]:
UT WY MT
Pronghorn fair poor ----
Elk fair fair ----
Mule deer good good ----
White-tailed deer ---- good ----
Small mammals fair good ----
Small nongame birds good good ----
Upland game birds good good ----
Waterfowl fair good good
VALUE FOR REHABILITATION OF DISTURBED SITES :
Sandbar willow's ability to rapidly colonize disturbed sites makes it
very useful for streambank stabilization projects. Cuttings are
preferred for use in revegetating disturbed riparian areas because they
quickly stabilize disturbed alluvium, which allows other plants to
become established. Unrooted willow stem cuttings (slips) should be
planted on sites that provide sufficient moisture to start and maintain
growth through the growing season [56]. Since willows are sensitive to
both competition and shading, dense tall grasses will reduce transplant
survival [47] and may need to be removed by cutting or by herbicide
application [34]. Although harder to plant, rooted stock is recommended
because it has higher survival rates [47,58]. Slips should be obtained
from local native stands. Cuttings should be planted 12 inches (30 cm)
deep, with 8 inches (20 cm) left above ground [47]. Planting deep
allows for more rooting surface to extract soil moisture and higher
amounts of carbohydrates as stored food reserves [47,58]. Sandbar
willow cuttings root along the entire length of the stem, with roots
appearing in about 10 days [23,47]. If serious streambank erosion has
caused a nearly verticle cut bank, reshaping of the slope may be needed
to enhance success of transplants; reshaping is not necessary if,
through protective measures, existing vegetation is able to stabilize
the site [47,58]. Under any method of revegetation, sites should be
fenced to protect them from grazing and trampling.
OTHER USES AND VALUES :
All willows produce salicin, which chemically is closely related to
acetylsalicylic acid, commonly known as aspirin. This is probably why
Native Americans used various preparations from willows to treat
toothache, stomach ache, diarrhea, dysentery, and dandruff [41]. Native
Americans also used the stems for basketry and bow making, and the bark
for tea and fabric making [34].
MANAGEMENT CONSIDERATIONS :
Stands of sandbar willow should be maintained because they help
stabilize streambanks and protect them from erosion. Once degredation
occurs, streambanks may erode rapidly [23].
BOTANICAL AND ECOLOGICAL CHARACTERISTICS
SPECIES: Salix exigua | Sandbar Willow
GENERAL BOTANICAL CHARACTERISTICS :
Sandbar willow is a short-lived deciduous shrub or small tree up to
about 26 feet (8 m) tall, with soft weak wood, and thin gray-green to
brown bark [7,54,62]. Staminate and pistillate flowers occur on
separate plants as catkins. The fruit is a narrowly ovoid capsule. The
three subspecies as a whole are characterized as (1) having numerous
slender stems, (2) forming thickets through the underground spread of
root suckers, and (3) having long and narrow mature leaves (5 to 20
times as long as wide) which are equally green on both surfaces
[7,10,23]. The three subspecies intergrade, making identification
difficult; general botanical characteristics of the subspecies include
[7,10,16,54,62]:
ssp. exigua ssp. interior ssp. melanopsis
Mature Height 6-12 f (2-4 m) 20 feet (6 m) 12 feet (4 m)
Mature Leaves lanceolate linear-lanceolate linear or oblong
entire/few toothed remotely dentate toothed/subentire
up to 13 cm long up to 12 cm long up to 12 cm long
Male Catkins 1-4.5 cm long 3-4 cm long 1.5-3.5 cm long
Female Catkins 1.5-6 cm long 2.5-3 cm long 2-4 cm long
Capsule 4-7 mm long 6-7.3 mm long 3-5 mm long
sessile pedicellate/glab. sessile/glabrous
Twigs of Season thin-dense sparse-moderate
pubescence,with pubescence,with
strait appressed loosely appressed
hairs wavy/curly hairs
RAUNKIAER LIFE FORM :
Undisturbed State: Phanerophyte (nanophanerophyte)
Undisturbed State: Phanerophyte (microphanerophyte)
Burned State: Hemicryptophyte
REGENERATION PROCESSES :
Sandbar willow is able to reproduce vegetatively by sprouting from
underground shoot buds which occur on lateral roots and produce male or
female clones. This method of vegetative reproduction (suckering) is
uncommon in willows and occurs only in section Longifoliae [1].
Suckering allows this plant to spread and form colonies or thickets that
may be several meters in diameter [1,10]. On a sandbar in Wisconsin
estimated to be approximately 45 to 50 years old, more than 97 percent
of sandbar willow (ssp. interior) stems sampled were clones 1 to 3 years
old [3]. Regeneration may also occur through broken pieces of stems and
roots which are transported and deposited by floodwaters and later
sprout. This is a common method of vegetative reproduction in willows
and may be important in initial colonization of some disturbed sites,
although seeding seems to be more important [65].
Reproduction occurs sexually through the production of numerous seeds.
Flowers are pollinated by insects, commonly by bees [41]. After
fertilization, a capsule develops which eventually splits open,
dispersing the numerous tiny seeds which are covered with a cottony down
which aids in their dispersal by wind and water [2,41]. The nondormant
seeds have a thin seed coat and germinate soon after being dispersed.
On adequate substrates most germinate within 24 hours [12]. Ware and
Penfound [59] found that seeds older than 1 week rarely germinated; thus
seeds must land on suitable sites quickly if they are to germinate.
Seeds kept at 32 to 41 degrees F (0-5 deg C) can be stored 4 to 6 weeks
[8]. Seeds require light for germination [8]. Fresh alluvium deposited
along rivers provides an ideal substrate for establishment. These sites
have constant soil moisture and generally have no overstory trees to
shade out this light-sensitive species [23].
SITE CHARACTERISTICS :
Sandbar willow is found almost exclusively in riparian habitats,
occupying banks of major rivers and smaller streams, lakes and ponds,
marshy areas, alluvial terraces, and ditches [16,23,54,64]. It
characteristically forms zones immediately adjacent to the water's edge.
These areas are subjected to periodic flooding which often deposits sand
and cobble below the high water mark. With severe annual flooding it
may be the only shrub to survive in this zone [10]. Although often
found below the high water mark, it must have a portion of its crown out
of the water during part of the summer to survive [52]. Sandbar willow
may also occur on moist, well-drained benches and bottomlands [10]. It
normally does not exist in the understory due to its shade intolerance,
and is generally replaced by cottonwoods.
Soils: Sandbar willow occurs on a wide range of soil textures, but
usually occurs on soils derived from alluvial or fluvial parent material
of mixed geologic origin [60]. In western Montana it is typically found
on coarse-textured substrates of sand or gravel, but in eastern Montana
it may occur on fine-textured silts [23]. It also occurs on a wide
range of soil types in eastern Idaho and western Wyoming. Sandbar
willow communities there occupied soils from fine-loamy or finer
textures, to coarse-textured soils with up to 35 percent rock fragments
[64].
Associates: Adjacent drier areas may be dominated by cottonwoods, green
ash (Fraxinus pennsylvanica), water birch (Betula occidentalis),
thinleaf alder (Alnus incana ssp. tenuifolia), and other willows
[23,64].
Elevation: Sites in the Intermountain West are typically at low to
mid-elevations. Stands in Montana, Wyoming, and Idaho are adjacent to
uplands commonly dominated by conifers, and big sagebrush (Artemisia
tridentata) and Idaho fescue (Festuca idahoensis) [10,24,43,64].
Elevational ranges for several western states are presented below
[10,14,24,25,42,42,48,62]:
2,700-8,500 feet (825-2,590 m) in UT
5,000-9,000 feet (1,524-2,743 m) in CO
8,000 feet (2,438 m) in s CA
3,200-6,700 feet (975-2,042 m) in MT
3,400-8,600 feet (1,036-2,621 m) in WY
ssp. exigua: below 6,000 feet (1,830 m) in east-central ID
ssp. melanopsis: 6,000-7,000 feet (1,830-2,130 m) in ec ID
ssp. exigua: 3,500 to 3,900 feet (1,067-1,181 m) Trans Pecos TX
ssp. interior: 1,800 to 3,600 feet (549-1,097 m) Trans Pecos TX
SUCCESSIONAL STATUS :
Sandbar willow is a pioneer species that colonizes new sand and gravel
bars. After initial colonization, it helps stabilize the sand and
gravel deposits, which allows other species to follow [49]. It may
dominate these disturbed areas for only a few years before being
replaced by cottonwoods. Repeated flooding may allow sandbar willow to
persist [24], but once cottonwoods become established it cannot
regenerate and establish itself. In Kansas, it occurs only as a
pioneer; stands there maintain themselves for about 10 years before
cottonwood becomes established and shades them out [4].
SEASONAL DEVELOPMENT :
Catkins of sandbar willow develop over a several weeks, with the first
expanding with the leaves and then continuing to develop as the leaves
mature [10]. Flowering times for several states follow [14]:
State Flowering Begins Flowering Ends
CO May July
MT May July
UT April July
WY May July
Noble [67] reported that in Minnesota seeds were shed from early June to
late July, which is commonly the time the rivers are dropping in
elevation and exposing moist substrates favorable for germination. Seed
dispersal probably coincides with local flooding patterns.
In Oklahoma Ware and Penfound [59] reported that plants produce leaves
by March 28, fruits by May 5, and seedlings by May 15.
FIRE ECOLOGY
SPECIES: Salix exigua | Sandbar Willow
FIRE ECOLOGY OR ADAPTATIONS :
Sandbar willow sprouts from its roots after fire [11,50,65]. Its
numerous wind-dispersed seeds are also important in revegetating burned
areas [50]. The high soil and fuel moisture content characteristic of
its steamside habitat reduces the chance of fire ingition and spread.
POSTFIRE REGENERATION STRATEGY :
survivor species; on-site surviving root crown or caudex
off-site colonizer; seed carried by wind; postfire years one and two
off-site colonizer; seed carried by animals or water; postfire yr 1&2
FIRE EFFECTS
SPECIES: Salix exigua | Sandbar Willow
IMMEDIATE FIRE EFFECT ON PLANT :
Most fires kill only aboveground plant parts. However, severe fires can
completely remove organic soil layers, leaving willow roots exposed and
charred, thus eliminating basal sprouting [4,5,6].
DISCUSSION AND QUALIFICATION OF FIRE EFFECT :
NO-ENTRY
PLANT RESPONSE TO FIRE :
Generally sandbar willow will sprout from its roots following fire
[50,65]. Irwin [30] found that sandbar willow was common in the boreal
forest of northeastern Minnesota 2 years after a May wildfire. Sandbar
willow is a prolific seeder; off-site plants are important as a seed
source for revegetating burned areas [65].
DISCUSSION AND QUALIFICATION OF PLANT RESPONSE :
NO-ENTRY
FIRE MANAGEMENT CONSIDERATIONS :
Due to its proximity to water or high water tables, sandbar willow
communities may serve as natural fire breaks [2].
REFERENCES
SPECIES: Salix exigua | Sandbar Willow
REFERENCES :
1. Argus, George W. 1973. The genus Salix in Alaska and the Yukon.
Publications in Botany, No. 2. Ottowa, ON: National Museums of Canada,
National Museum of Natural Sciences. 279 p. [6167]
2. Arno, Stephen F.; Hammerly, Ramona P. 1977. Northwest trees. Seattle,
WA: The Mountaineers. 222 p. [4208]
3. Barnes, W. J. 1985. Population dynamics of woody plants on a river
island. Canadian Journal of Botany. 63: 647-655. [2855]
4. Bellah, R. Glenn; Hulbert, Lloyd C. 1974. Forest succession on the
Republican River floodplain in Clay County, Kansas. Southwestern
Naturalist. 19(2): 155-166. [241]
5. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals,
reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's
associations for the eleven western states. Tech. Note 301. Denver, CO:
U.S. Department of the Interior, Bureau of Land Management. 169 p.
[434]
6. Boyd, Raymond J.; Cooperrider, Allen Y.; Lent, Peter C.; Bailey, James
A. 1986. Ungulates. In: Cooperrider, Allen Y.; Boyd, Raymond J.; Stuart,
Hanson R., eds. Inventory and monitoring of wildlife habitat. Denver,
CO: U.S. Department of the Interior, Bureau of Land Management, Service
Center: 519-564. [10856]
7. Brayshaw, T. Christopher. 1976. Catkin bearing plants of British
Columbia. Occas. Pap. No. 18. Victoria, BC: The British Columbia
Provincial Museum. 176 p. [6170]
8. Brinkman, Kenneth A. 1974. Salix L. willow. In: Schopmeyer, C. S.,
technical coordinator. Seeds of woody plants in the United States.
Agric. Handb. 450. Washington, DC: U.S. Department of Agriculture,
Forest Service: 746-750. [5412]
9. Brown, David E. 1979. Southwestern wetlands - their classification and
characteristics. In: Johnson, R. Roy; McCormick, J. Frank, technical
coordinators. Strategies for protection and management of floodplain
wetlands & other riparian ecosystems: Proc. of the symposium; 1978
December 11-13; Callaway Gardens, GA. Gen. Tech. Rep. WO-12. Washington,
DC: U.S. Department of Agriculture, Forest Service: 269-282. [4366]
10. Brunsfeld, Steven J.; Johnson, Frederic D. 1985. Field guide to the
willows of east-central Idaho. Bulletin Number 39. Moscow, ID:
University of Idaho; College of Forestry, Wildlife and Range Sciences;
Forest, Wildlife and Range Experiment Station. 82 p. [6175]
11. Conrad, C. Eugene. 1987. Common shrubs of chaparral and associated
ecosystems of southern California. Gen. Tech. Rep. PSW-99. Berkeley, CA:
U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest
and Range Experiment Station. 86 p. [4209]
12. Densmore, Roseann; Zasada, John. 1983. Seed dispersal and dormancy
patterns in northern willows: ecological and evolutionary significance.
Canadian Journal of Botany. 61: 3207-3216. [5027]
13. Dirschl, German J.; Dabbs, Don L.; Gentle, Garry C. 1974. Landscape
classification and plant successional trends in the Peace-Athabasca
Delta. Canadian Wildlife Service Report Series 30. Ottawa, ON: Canadian
Wildlife Service. 33 p. [6177]
14. Dittberner, Phillip L.; Olson, Michael R. 1983. The plant information
network (PIN) data base: Colorado, Montana, North Dakota, Utah, and
Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior,
Fish and Wildlife Service. 786 p. [806]
15. Dorn, Robert D. 1976. A synopsis of American Salix. Canadian Journal of
Botany. 54: 2769-2789. [4457]
16. Dorn, Robert D. 1977. Willows of the Rocky Mountain States. Rhodora. 79:
390-429. [6000]
17. Eyre, F. H., ed. 1980. Forest cover types of the United States and
Canada. Washington, DC: Society of American Foresters. 148 p. [905]
18. Finch, Deborah M. 1987. Bird-habitat relationships in subalpine riparian
shrublands of the central Rocky Mountains. In: Troendle, Charles A.;
Kaufmann, Merrill R.; Hamre, R. H.; Winokur, Robert P., technical
coordinators. Management of subalpine forests: building on 50 years of
research: Proceedings of a technical conference; 1987 July 6-9; Silver
Creek, CO. Gen. Tech. Rep. RM-149. Fort Collins, CO: U.S. Department of
Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment
Station: 167-172. [3475]
19. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others].
1977. Vegetation and environmental features of forest and range
ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of
Agriculture, Forest Service. 68 p. [998]
20. Geyer, Wayne A. 1989. Biomass yield potential of short-rotation
hardwoods in the Great Plains. Biomass. 20: 167-175. [10135]
21. Gray, M. Violet; Greaves, James M. 1984. Riparian forest as habitat for
the least Bell's vireo. In: Warner, Richard E.; Hendrix, Kathleen M.,
eds. California riparian systems: Ecology, conservation, and productive
management: Proceedings of a conference; 1981 September 17-19; Davis,
CA. Berkeley, CA: University of California Press: 605-611. [5862]
22. Great Plains Flora Association. 1986. Flora of the Great Plains.
Lawrence, KS: University Press of Kansas. 1392 p. [1603]
23. Hansen, Paul L.; Chadde, Steve W.; Pfister, Robert D. 1988. Riparian
dominance types of Montana. Misc. Publ. No. 49. Missoula, MT: University
of Montana, School of Forestry, Montana Forest and Conservation
Experiment Station. 411 p. [5660]
24. Hansen, Paul; Chadde, Steve; Pfister, Robert; [and others]. 1988.
Riparian site types, habitat types, and community types of southwestern
Montana. Missoula, MT: University of Montana, School of Forestry,
Montana Riparian Association. 140 p. [5883]
25. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed.
Chicago: The Swallow Press Inc. 666 p. [6851]
26. Hess, Karl; Alexander, Robert R. 1986. Forest vegetation of the Arapaho
and Roosevelt National Forests in central Colorado: a habitat type
classification. Res. Pap. RM-266. Fort Collins, CO: U.S. Department of
Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment
Station. 48 p. [1141]
27. Hitchcock, C. Leo; Cronquist, Arthur. 1964. Vascular plants of the
Pacific Northwest. Part 2: Salicaceae to Saxifragaceae. Seattle, WA:
University of Washington Press. 597 p. [1166]
28. Hosner, John F.; Minckler, L. S. 1960. Hardwood reproduction in the
river bottoms of southern Illinois. Forest Science. 6(1): 67-77. [3738]
29. Houston, Douglas B. 1968. The Shiras Moose in Jackson Hole, Wyoming.
Tech. Bull. No. 1. [Place of publication unknown]: The Grand Teton
Natural History Association. 110 p. [7824]
30. Irwin, Larry L. 1985. Foods of moose, Alces alces, and white-tailed
deer, Odocoileus virginianus, on a burn in boreal forest. Canadian
Field-Naturalist. 99(2): 240-245. [4513]
31. Komarkova, Vera; Alexander, Robert R.; Johnston, Barry C. 1988. Forest
vegetation of the Gunnison and parts of the Uncompahgre National
Forests: a preliminary habitat type classification. Gen. Tech. Rep.
RM-163. Fort Collins, CO: U.S. Department of Agriculture, Forest
Service, Rocky Mountain Forest and Range Experiment Station. 65 p.
[5798]
32. Kovalchik, Bernard L. 1987. Riparian zone associations: Deschutes,
Ochoco, Fremont, and Winema National Forests. R6 ECOL TP-279-87.
Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific
Northwest Region. 171 p. [9632]
33. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation
of the conterminous United States. Special Publication No. 36. New York:
American Geographical Society. 77 p. [1384]
34. Lanner, Ronald M. 1983. Trees of the Great Basin: A natural history.
Reno, NV: University of Nevada Press. 215 p. [1401]
35. Lindauer, Ivo E. 1983. A comparison of the plant communities of the
South Platte and Arkansas River drainages in eastern Colorado.
Southwestern Naturalist. 28(3): 249-259. [5886]
36. Little, Elbert L., Jr. 1979. Checklist of United States trees (native
and naturalized). Agric. Handb. 541. Washington, DC: U.S. Department of
Agriculture, Forest Service. 375 p. [2952]
38. Lyon, L. Jack; Stickney, Peter F. 1976. Early vegetal succession
following large northern Rocky Mountain wildfires. In: Proceedings, Tall
Timbers fire ecology conference and Intermountain Fire Research Council
fire and land management symposium; 1974 October 8-10; Missoula, MT. No.
14. Tallahassee, FL: Tall Timbers Research Station: 355-373. [1496]
39. Medina, Alvin L. 1986. Riparian plant communities of the Fort Bayard
watershed in southwestern New Mexico. Southwestern Naturalist. 31(3):
345-359. [1629]
40. Monsen, Stephen B. 1983. Plants for revegetation of riparian sites
within the Intermountain region. In: Monsen, Stephen B.; Shaw, Nancy,
compilers. Managing Intermountain rangelands--improvement of range and
wildlife habitats: Proceedings of symposia; 1981 September 15-17; Twin
Falls, ID; 1982 June 22-24; Elko, NV. Gen. Tech. Rep. INT-157. Ogden,
UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest
and Range Experiment Station: 83-89. [9652]
41. Mozingo, Hugh N. 1987. Shrubs of the Great Basin: A natural history.
Reno, NV: University of Nevada Press. 342 p. [1702]
42. Munz, Philip A. 1974. A flora of southern California. Berkeley, CA:
University of California Press. 1086 p. [4924]
43. Padgett, Wayne G.; Youngblood, Andrew P.; Winward, Alma H. 1989.
Riparian community type classification of Utah and southeastern Idaho.
R4-Ecol-89-01. Ogden, UT: U.S. Department of Agriculture, Forest
Service, Intermountain Region. 191 p. [11360]
44. Pase, Charles P.; Layser, Earle F. 1977. Classification of riparian
habitat in the Southwest. In: Johnson, Roy; Jones, Dale A., technical
coordinators. Importance, preservation and management of riparian
habitat: A symposium; 1977 July 9; Tucson, AZ. Gen. Tech. Rep. RM-43.
Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky
Mountain Forest and Range Experiment Station: 5-9. Available from: NTIS,
Springfield, VA 22151; PB-274 582. [5333]
45. Patten, D. T. 1968. Dynamics of the shrub continuum along the Gallatin
River in Yellowstone National Park. Ecology. 49(6): 1107-1112. [1837]
45. Peek, J. M. 1974. A review of moose food habits studies in North
America. Le Naturaliste Canadien. 101: 195-215. [7420]
46. Petranka, James W.; Holland, Robert. 1980. A quantitative analysis of
bottomland communities in south-central Oklahoma. Southwestern
Naturalist. 25(2): 207-214. [5885]
47. Platts, William S.; Armour, Carl; Booth, Gordon D.; [and others]. 1987.
Methods for evaluating riparian habitats with applications to
management. Gen. Tech. Rep. INT-221. Ogden, UT: U.S. Department of
Agriculture, Forest Service, Intermountain Research Station. 177 p.
[6171]
48. Powell, A. Michael. 1988. Trees & shrubs of Trans-Pecos Texas including
Big Bend and Guadalupe Mountains National Parks. Big Bend National Park,
TX: Big Bend Natural History Association. 536 p. [6130]
49. Raunkiaer, C. 1934. The life forms of plants and statistical plant
geography. Oxford: Clarendon Press. 632 p. [2843]
50. Rowe, J. S.; Scotter, G. W. 1973. Fire in the boreal forest. Quaternary
Research. 3: 444-464. [72]
51. Sampson, Arthur W.; Jespersen, Beryl S. 1963. California range
brushlands and browse plants. Berkeley, CA: University of California,
Division of Agricultural Sciences, California Agricultural Experiment
Station, Extension Service. 162 p. [3240]
52. Shelford, V. E. 1954. Some lower Mississippi valley flood plain biotic
communities; their age and elevation. Ecology. 35(2): 126-142. [4329]
53. Smith, Arthur D. 1953. Consumption of native forage species by captive
mule deer during summer. Journal of Range Management. 6: 30-37. [2161]
54. Stephens, H. A. 1973. Woody plants of the North Central Plains.
Lawrence, KS: The University Press of Kansas. 530 p. [3804]
55. Szaro, Robert C.; Patton, David R. 1986. Riparian habitat classification
in the southwestern United States. Transactions of the 51st North
American Wildlife and Natural Resources Conference: 215-221. [3516]
56. U.S. Department of Agriculture, Forest Service. 1937. Range plant
handbook. Washington, DC. 532 p. [2387]
57. Van Dersal, William R. 1938. Native woody plants of the United States,
their erosion-control and wildlife values. Washington, DC: U.S.
Department of Agriculture. 362 p. [4240]
58. Ward, Don; Thompson, Robert; Kelly, Dennis. 1986. Willow planting guide.
R-4 Hydrograph No. 54. Ogden, UT: U.S. Department of Agriculture, Forest
Service, Range and Watershed Management. 12 p. [2936]
59. Ware, George H.; Penfound, W. T. 1949. The vegetation of the lower
levels of the floodplain of the South Canadian River in Central
Oklahoma. Ecology. 30: 478-484. [6004]
60. Wasser, C. H.; Hess, Karl. 1982. The habitat types of Region II, U.S.
Forest Service: a synthesis. Final Report Cooperative Agreement No.
16-845-CA. Lakewood, CO: U.S. Department of Agriculture, Forest Service,
Region 2. 140 p. [5594]
61. Weaver, J. E. 1960. Flood plain vegetation of the central Missouri
Valley and contacts of woodland with prairie. Ecological Monographs.
30(1): 37-64. [275]
62. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry
C., eds. 1987. A Utah flora. Great Basin Naturalist Memoir No. 9. Provo,
UT: Brigham Young University. 894 p. [2944]
63. White, W. W. 1956. Native willows found in Montana. Proceedings of the
Montana Academy of Science. 16: 21-35. [6001]
64. Youngblood, Andrew P.; Padgett, Wayne G.; Winward, Alma H. 1985.
Riparian community type classification of eastern Idaho - western
Wyoming. R4-Ecol-85-01. Ogden, UT: U.S. Department of Agriculture,
Forest Service, Intermountain Region. 78 p. [2686]
65. Zasada, J. 1986. Natural regeneration of trees and tall shrubs on forest
sites in interior Alaska. In: Van Cleve, K.; Chapin, F. S., III;
Flanagan, P. W.; [and others], eds. Forest ecosystems in the Alaska
taiga: A synthesis of structure and function. New York: Springer-Verlag:
44-73. [2291]
66. U.S. Department of Agriculture, Soil Conservation Service. 1982.
National list of scientific plant names. Vol. 1. List of plant names.
SCS-TP-159. Washington, DC. 416 p. [11573]
67. Noble, Mark G. 1979. The origin of Populus deltoides and Salix interior
zones on point bars along the Minnesota River. American Midland
Naturalist. 102: 59-67. [6172]
Index
Related categories for Species: Salix exigua
| Sandbar Willow
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