Wildlife, Animals, and Plants
|
|
Introductory
SPECIES: Salix nigra | Black Willow
ABBREVIATION :
SALNIG
SYNONYMS :
NO-ENTRY
SCS PLANT CODE :
SANI
COMMON NAMES :
black willow
swamp willow
southwestern black willow
Gulf black willow
scythe-leaved willow
TAXONOMY :
The currently accepted scientific name of black willow is Salix nigra
Marsh. [11,12,22,26,31]. Recognized varieties are S. nigra var. nigra
Marsh., S. nigra var. altissima Sarg., S. nigra var. falcata (Pursh.)
Torr., and S. nigra var. lindheimeri [20,22,26].
Salix nigra, S. gooddingii Ball, and S. amygdaloides Anderss. are
closely related taxa commonly referred to as the black willows [26].
The three species are not easily distinguished morphologically, and in
fact, some authorities consider S. gooddingii to be S. nigra var.
vallicola Dudley or S. n. var. venulosa (Anderss.) Bebb. [5,8,36]. S.
amygdaloides is sometimes considered to be S. nigra var. amygdaloides
Anderss. [13]. For our purposes, however, these varieties will be
considered as separate species. S. nigra hybridizes with S.
amygdaloides (S. X glatfelteri Schneider); S. alba (S. X hankensonii
Dode); and S. lucida (S. X schneider Boivin) [5,20,38].
LIFE FORM :
Tree, Shrub
FEDERAL LEGAL STATUS :
No special status
OTHER STATUS :
NO-ENTRY
COMPILED BY AND DATE :
Julie L. Tesky, April 1992.
LAST REVISED BY AND DATE :
NO-ENTRY
AUTHORSHIP AND CITATION :
Tesky, Julie L. 1992. Salix nigra. In: Remainder of Citation
DISTRIBUTION AND OCCURRENCE
SPECIES: Salix nigra | Black Willow
GENERAL DISTRIBUTION :
Black willow is found throughout the eastern United States, adjacent
parts of Canada, and Mexico. Its range extends west from southern New
Brunswick and central Maine to Quebec, southern Ontario, central
Michigan, southeastern Minnesota, and eastern North Dakota. It occurs
south and west to the Rio Grande just below its confluence with the
Pecos River; and east along the Gulf Coast through the Florida Panhandle
and southern Georgia [5,8,11]. Black willow has been introduced in Utah
where it is now common along many streambottoms [17].
ECOSYSTEMS :
FRES16 Oak - gum - cypress
FRES17 Elm - ash - cottonwood
FRES36 Mountain grasslands
FRES41 Wet grasslands
STATES :
AL AR CT DE FL GA IL IN IA KS
KY LA ME MD MA MI MN MS MO NE
NH NJ NY NC ND OH OK PA RI SC
TN TX UT VT VA WV WI MB NB ON
PQ MEXICO
ADMINISTRATIVE UNITS :
AMIS ASIS BISO BITH BLRI BUFF
CACO CARE CATO CHCH COLO COSW
CUGA CUVA DEWA EFMO FODO GATE
GWCA GWMP GRSM HOBE INDU JELA
LAMR MACA MORR NATR NERI OBRI
OZAR PAIS PIPE PRWI RICH ROCR
SHEN SHIL VAFO WICR
BLM PHYSIOGRAPHIC REGIONS :
6 Upper Basin and Range
12 Colorado Plateau
14 Great Plains
16 Upper Missouri Basin and Broken Lands
KUCHLER PLANT ASSOCIATIONS :
K091 Cypress savanna
K092 Everglades
K098 Northern floodplain forest
K101 Elm - ash forest
K113 Southern floodplain forest
SAF COVER TYPES :
61 River birch - sycamore
63 Cottonwood
94 Sycamore - sweetgum - American elm
95 Black willow
101 Baldcypress
102 Baldcypress - tupelo
103 Water tupelo - swamp tupelo
235 Cottonwood - willow
SRM (RANGELAND) COVER TYPES :
NO-ENTRY
HABITAT TYPES AND PLANT COMMUNITIES :
Black willow occurs as a codominant in some early seral floodplain
communities [24,30]. It codominates with sandbar willow (Salix exigua)
on floodplains having the greatest water depths and the longest
hydroperiods of any of the shallow freshwater swamps of the southern
United States [24]. Black willow also codominates with eastern
cottonwood (Populus deltoides) in the lower Mississippi Valley [30].
Published classifications listing black willow as a codominant in
community types (cts) are listed below:
Area Classification Authority
S. U.S. southern swamp & Penfound 1952
marsh cts
AR,MS: Lower cts Shelford 1954
Mississippi Valley
VALUE AND USE
SPECIES: Salix nigra | Black Willow
WOOD PRODUCTS VALUE :
Black willow is the largest and only commercially important willow in
North America. The wood is light, usually straight grained, and
moderately high in shock resistance. It stains and finishes well but is
relatively undurable [5]. The wood was once used extensively for
artifical limbs because it is lightweight, does not splinter easily, and
holds its shape well [5,8]. It is still used for making boxes and
crates, furniture core stock, turned pieces, table tops, wooden
novelties, doors, cabinets, polo balls, and toys [5,8,15]. Black willow
is also used for pulp [5,8].
IMPORTANCE TO LIVESTOCK AND WILDLIFE :
Birds eat the buds and flowering catkins of black willow; deer eat the
twigs and leaves; and rodents eat the bark and buds [8,35]. The
yellow-bellied sapsucker feeds on the sap [5,39]. Black willow is
somewhat tolerant of grazing and browsing [39]. Black willow/cottonwood
stands are also commonly used as nesting habitat by some small nongame
bird species [30].
PALATABILITY :
Palatability of black willlow has been rated as fair for livestock and
deer [7,39].
NUTRITIONAL VALUE :
Black willow has been rated as fair in energy value and poor in protein
value [7].
COVER VALUE :
Black willow cover values in Utah are rated as follows [7]:
pronghorn - poor
elk - poor
moose - fair
small mammals - fair
small nongame birds - good
upland game birds - good
waterfowl - fair
VALUE FOR REHABILITATION OF DISTURBED SITES :
Black willow was commonly used in soil stabilization projects in early
efforts at erosion control. Its flood tolerance and the ease with which
it establishes from cuttings continue to make it an excellent species
for reducing erosion of streambanks, bars, and islands [5,8,18,39].
Post-sized willow cuttings have been rooted for use in flood projects to
prevent gullies from forming [5].
Seeds lose viability rapidly if stored at room temperature.
Refrigerated storage of moistened seeds for no longer than 1 month is
recommended. Commercial seed is not usually available [39]. Planted
seedlings or cuttings should be protected from livestock, beavers, small
rodents, and rabbits. Hardware cloth placed around individual plants
will protect them from rodents and rabbits. Livestock should be
excluded by fencing the entire area, and firebreaks should surround the
revegetated area. Additionally, the area around each tree should be
kept free of weeds [18]. To reduce competition densities greater than
494 to 556 trees per acre (200-225 trees/ha) should be avoided [18].
OTHER USES AND VALUES :
Ancient pharmacopoeia recognized the bark and leaves of willow as useful
in the treatment of rheumatism [5]. Pioneering settlers boiled the bark
of black willow for its purgative and vermin-destroying powers [40]. In
1829, the natural glucoside, salicin, which is closely related
chemically to aspirin, was isolated from willow [5]. Black willow was
once used as a source of charcoal for gunpowder [8].
MANAGEMENT CONSIDERATIONS :
Thinning: To increase yields and reduce mortality of black willow,
stands should be thinned as soon as economically feasible; thinning
should continue at 5-year intervals [5,28]. Spacing between trees after
thinning should average about 21 times the mean stem diameter of 10
inches (25.4 cm). This results in a 17.5 feet (5.3 m) spacing [5].
Insects and Disease: The forest tent caterpillar (malacosoma disstria),
the gypsy moth (Lymantria dispar), the cottonwood leaf beetle
(Chrysomila scripta), the willow sawfly (Nematus ventralis), and the
willow leaf beetle (Plagiodera versicolora) partially or occasionally
completely defoliate willow trees, reducing growth but seldom causing
death. The cottonwood borer (Plectrodera scalator) attacks black willow
and may kill by girdling the base. Top and branch rot account for 86
percent of the cull in willow. Leaf rust, fungus scab, and black canker
can cause leaf and shoot destruction of black willow seedlings [5,39].
Because of its weak wood and shallow roots, black willow is susceptible
to breakage and windthrow [39].
BOTANICAL AND ECOLOGICAL CHARACTERISTICS
SPECIES: Salix nigra | Black Willow
GENERAL BOTANICAL CHARACTERISTICS :
Black willow is a small (sometimes shrublike) to large, short-lived,
deciduous tree [3,5,8,27,29]. It is fast growing and may reach maturity
within 30 years [8,17]. This tree usually obtains a height of 66 feet
(20 m) but can grow up to 138 feet (42 m) on some sites [8]. The
massive trunks are usually leaning and are often divided. The bark is
thick and deeply divided into furrows separating thick, scaly ridges.
The crown is broad and open with stout branches [27]. Twigs are slender
and easily detached [8]. Leaf blades are variable in size, the larger
to 4.7 inches (12 cm) long. Black willow roots are shallow and
laterally extensive [5,39].
RAUNKIAER LIFE FORM :
Phanerophyte (mesophanerophyte)
Phanerophyte (microphanerophyte)
Phanerophyte (nanophanerophyte)
REGENERATION PROCESSES :
Sexual reproduction: Black willows start producing seed when they are
about 10 years old [4,5]. Optimum seed-bearing age is from 25 to 75
years. The trees have good seed crops almost every year. producing an
average of 2.3 million seeds per pound (5 million/kg). Seeds ripen 45
to 60 days after catkins are pollinated by insects or wind. As the
seeds fall, the long silky hairs act as wings to carry the seeds long
distances. The seeds are also disseminated by water [5].
Seeds are not dormant. Viability is greatly reduced by only a few days
of dry conditions. Germination is epigeal, and germination capacity is
usually high. Very moist bare mineral soil is best for germination and
early development [5,14,28]. Once seedlings are established, full light
promotes vigorous growth. Seedlings grow rapidly in a favorable
environment, often exceeding 4 feet (1.2 m) in the first year. Low
ground cover competition and shade, however, greatly hampers growth
[28].
Vegetative reproduction: Root stocks of very young black willow trees
sprout prolifically. Propagation by cutting is the usual method of
artifical regeneration [5,39].
SITE CHARACTERISTICS :
Black willow is most common on river margins where it occupies the
lower, wetter, and often less sandy sites. It is also common in swamps,
sloughs, swales, gullies, and drainage ditches, growing anywhere light
and moisture conditions are favorable [5]. It flourishes at or slightly
below water level and is not appreciably damaged by flooding and silting
[5,16]. On a flooded site in southern Illinois, black willow survived
32 or more days of complete inundation [16]. Black willow, however, is
not drought tolerant. Whole stands may die out when water tables lower
and soil drys up [39].
Soils: Black willow grows on a variety of soils but develops best in
fine silt or clay in relatively stagnant water. It thrives in saturated
or poorly drained soil from which other hardwoods are excluded [6,24].
Black willow is commonly found in moderately acidic (lower pH limit is
4.5) to near neutral soils [5].
Climate: Black willow grows best in climates characterized by an
average annual rainfall of 51 inches (130 cm), with approximately 20
inches (51 cm) falling from April through August. The average maximum
temperature across its range is 93 degrees Fahrenheit (34 deg C) in the
summer and 59 degrees Fahrenheit (15 deg C) in the winter [5].
Plant associates: Black willow is commonly associated with the
following species: eastern cottonwood, red maple (Acer rubrum), black
spruce (Picea mariana), river birch (Betula nigra), American sycamore
(Platanus occidentalis), boxelder (Acer negundo), red mulberry (Morus
rubra), swamp privet (Forestiera acuminata), buttonbush (Cephalanthus
occidentalis), water elm (Planera aquatica), and American elm (Ulmus
americana) [5,39].
SUCCESSIONAL STATUS :
Black willow is a pioneer or early seral species commonly found along
the edges of rivers and streams, mud flats, and floodplains. This tree
is very shade intolerant and usually grows in dense, even-aged stands.
Black willow stands periodically stagnate and are eventually replaced by
more shade-tolerant trees such as American elm, sycamore (Platanus
spp.), ash (Fraxinus spp.), boxelder, and sweet gum (Liquidambar
styraciflua) [5,14,32,34,41].
SEASONAL DEVELOPMENT :
Black willow flowering begins in February in the southern portion of its
range and extends through late June at the northern limits. The catkins
usually appear at the time of or immediately preceding leaf emergence
[5,39]. Seeds ripen and fall in April to July [39].
FIRE ECOLOGY
SPECIES: Salix nigra | Black Willow
FIRE ECOLOGY OR ADAPTATIONS :
Black willow has the ability to sprout from the base following fire
[37]. Its wind- and water-dispersed seeds are also important in
revegetating areas following fire. Fires are rare in the bottomland
areas where black willow typically occurs [1].
POSTFIRE REGENERATION STRATEGY :
survivor species; on-site surviving root crown or caudex
off-site colonizer; seed carried by wind; postfire years 1 and 2
off-site colonizer; seed carried by animals or water; postfire yr 1&2
FIRE EFFECTS
SPECIES: Salix nigra | Black Willow
IMMEDIATE FIRE EFFECT ON PLANT :
Although black willow does exhibit some fire adaptations, it is very
susceptible to fire damage and will typically decrease following fire
[1]. High-severity fires can kill entire stands of black willow.
Low-severity fires can scorch the bark and seriously wound trees,
leaving them more susceptible to insects and disease [5,37]. Surface
fires will also destroy young seedlings and saplings [5,24,37].
DISCUSSION AND QUALIFICATION OF FIRE EFFECT :
NO-ENTRY
PLANT RESPONSE TO FIRE :
Black willow will sprout from the base following fire [5,37]. Fires
that expose bare mineral soil may create a favorable seedbed for black
willow establishment. However, because seed viability is greatly
reduced by dry conditions [5], seedling establishment on burned sites
depends on the season of the burn, amount of moisture available, and
amount of exposed mineral soil.
DISCUSSION AND QUALIFICATION OF PLANT RESPONSE :
Following a spring fast-moving head fire in a palm (Sabal spp.) grove in
south Texas, all black willow trees up to 13 feet (4 m) tall were
scorched badly and had few green leaves. Three months after the fire
all aboveground portions of black willow trees had died, but almost all
sprouted from the base. Following a low to moderate-severity Oklahoma
grassland summer fire, black willow density decreased. Preburn density
was 169 stems per acre (417 stems/ha); a year following the burn density
was only 51 stems per acre (125 stems/ha) [1].
FIRE MANAGEMENT CONSIDERATIONS :
Burning has been shown to be beneficial in maintaining tallgrass
prairies by inhibiting the invasion of black willow and other woody
species [1].
REFERENCES
SPECIES: Salix nigra | Black Willow
REFERENCES :
1. Adams, Dwight E.; Anderson, Roger C.; Collins, Scott L. 1982.
Differential response of woody and herbaceous species to summer and
winter burning in an Oklahoma grassland. Southwestern Naturalist. 27:
55-61. [6282]
2. 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]
3. Braun, E. Lucy. 1961. The woody plants of Ohio. Columbus, OH: Ohio State
University Press. 362 p. [12914]
4. 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]
5. Burns, Russell M.; Honkala, Barbara H., tech. coords. 1990. Silvics of
North America. Vol 2. Hardwoods. Agric. Handb. 654. Washington, DC: U.S.
Department of Agriculture, Forest Service. 877 p. [13955]
6. Dionigi, Cristopher P.; Mendelssohn, Irving A.; Sullivan, Victoria I.
1985. Effects of soil waterlogging on the energy status and distribution
of Salix nigra and S. exigua in the Atchafalaya River Basin of
Louisiana. American Journal of Botany. 72(1): 109-119. [5889]
7. 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]
8. Duncan, Wilbur H.; Duncan, Marion B. 1988. Trees of the southeastern
United States. Athens, GA: The University of Georgia Press. 322 p.
[12764]
9. Eyre, F. H., ed. 1980. Forest cover types of the United States and
Canada. Washington, DC: Society of American Foresters. 148 p. [905]
10. 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]
11. Godfrey, Robert K. 1988. Trees, shrubs, and woody vines of northern
Florida and adjacent Georgia and Alabama. Athens, GA: The University of
Georgia Press. 734 p. [10239]
12. Godfrey, Robert K.; Wooten, Jean W. 1981. Aquatic and wetland plants of
southeastern United States: Dicotyledons. Athens, GA: The University of
Georgia Press. 933 p. [16907]
13. Hitchcock, C. Leo; Cronquist, Arthur. 1961. Vascular plants of the
Pacific Northwest. Part 3: Saxifragaceae to Ericaceae. Seattle, WA:
University of Washington Press. 614 p. [1167]
14. Hodges, John D.; Switzer, George L. 1979. Some aspects of the ecology of
southern bottomland hardwoods. In: North America's forests: gateway to
opportunity: Proceedings, 1978 joint convention of the Society of
American Foresters and the Canadian Institute of Forestry. Washington,
DC: Society of American Foresters: 360-365. [10028]
15. Hosie, R. C. 1969. Native trees of Canada. 7th ed. Ottawa, ON: Canadian
Forestry Service, Department of Fisheries and Forestry. 380 p. [3375]
16. Hosner, John F. 1958. The effects of complete inundation upon seedlings
of six bottomland tree species. Ecology. 39(2): 371-373. [115]
17. Johnson, Carl M. 1970. Common native trees of Utah. Special Report 22.
Logan, UT: Utah State University, College of Natural Resources,
Agricultural Experiment Station. 109 p. [9785]
18. Kerpez, Theodore A.; Smith, Norman S. 1987. Saltcedar control for
wildlife habitat improvement in the southwestern United States. Resource
Publication 169. Washington, DC: United States Department of Interior,
Fish and Wildlife Service. 16 p. [3039]
19. 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]
20. 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]
21. 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]
22. Mason, Herbert L. 1957. A flora of the marshes of California. Berkeley,
CA: University of California Press. 878 p. [16905]
23. Myers, Charles C.; Buchman, Roland G. 1984. Manager's handbook for
elm-ash-cottonwood in the North Central States. Gen. Tech. Rep. NC-98.
St. Paul, MN: U.S. Department of Agriculture, Forest Service, North
Central Forest Experiment Station. 11 p. [8919]
24. Penfound, William T. 1952. Southern swamps and marshes. The Botanical
Review. 18: 413-446. [11477]
25. Penfound, W. T.; Hathaway, Edward S. 1938. Plant communities in the
marshlands of southeastern Louisiana. Ecological Monographs. 8(1): 3-56.
[15089]
26. 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]
27. Preston, Richard J., Jr. 1948. North American trees. Ames, IA: The Iowa
State College Press. 371 p. [1913]
28. Putnam, John A. 1951. Management of bottomland hardwoods. Occasional
Paper 116. New Orleans, LA: U.S. Department of Agriculture, Forest
Service, Southern Forest Experiment Station. 60 p. [6748]
29. Raunkiaer, C. 1934. The life forms of plants and statistical plant
geography. Oxford: Clarendon Press. 632 p. [2843]
30. Shelford, V. E. 1954. Some lower Mississippi valley flood plain biotic
communities; their age and elevation. Ecology. 35(2): 126-142. [4329]
31. Simpson, Benny J. 1988. A field guide to Texas trees. Austin, TX: Texas
Monthly Press. 372 p. [11708]
32. Thomson, Paul M.; Anderson, Roger C. 1976. An ecological investigation
of the Oakwood Bottoms Greentree Reservoir in Illinois. In: Fralish,
James S.; Weaver, George T.; Schlesinger, Richard C., eds. Central
hardwood forest conference: Proceedings of a meeting; 1976 October
17-19; Carbondale, IL. Carbondale, IL: Southern Illinois University:
45-64. [3812]
33. 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]
34. Van Auken, O. W.; Bush, J. K. 1988. Dynamics of establishment, growth,
and development of black willow and cottonwood in the San Antonio River
Forest. Texas Journal of Science. 40(3): 269-277. [11138]
35. 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]
36. Vines, Robert A. 1960. Trees, shrubs, and woody vines of the Southwest.
Austin, TX: University of Texas Press. 1104 p. [7707]
37. Vora, Robin S. 1989. Fire in an old field adjacent to a sabal palm grove
in south Texas. Texas Journal of Science. 41(1): 107-108. [7063]
38. Voss, Edward G. 1985. Michigan flora. Part II. Dicots
(Saururaceae--Cornaceae). Bull. 59. Bloomfield Hills, MI: Cranbrook
Institute of Science; Ann Arbor, MI: University of Michigan Herbarium.
724 p. [11472]
39. Wasser, Clinton H. 1982. Ecology and culture of selected species useful
in revegetating disturbed lands in the West. FWS/OBS-82/56. Washington,
DC: U.S. Department of the Interior, Fish and Wildlife Service. 347 p.
[15400]
40. Walker, Laurence C. 1991. The southern forest: A chronicle. Austin, TX:
University of Texas Press. 322 p. [17597]
41. White, David A. 1989. Accreting mudflats at the Mississippi River Delta:
sedimentation rates and vascular plant succession. U.S. Fish and
Wildlife Service: Biological Report. 89(22): 49-57. [17336]
Index
Related categories for Species: Salix nigra
| Black Willow
|
|