Difference between revisions of "Solidago altissima"

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==Conservation and Management==
 
==Conservation and Management==
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Mowing does not effect the growth, survival, or reproduction of juvenile or seedling plants.<ref name="Meyer & Schmid 1999"/>
  
 
==Cultivation and restoration==
 
==Cultivation and restoration==

Revision as of 12:26, 19 January 2018

Solidago altissima
Solidago canadensis resized.jpg
Photo by Kevin Robertson
Scientific classification
Kingdom: Plantae
Division: Magnoliophyta - Flowering plants
Class: Magnoliopsida - Dicots
Order: Asterales
Family: Asteraceae
Genus: Solidago
Species: S. altissima
Binomial name
Solidago altissima
L.
SOLI ALTI DIST.JPG
Natural range of Solidago altissima from USDA NRCS Plants Database.

Common Name(s): tall goldenrod; Great Plains tall goldenrod; southern tall goldenrod;[1] Canada goldenrod;[2] Canadian goldenrod; late goldenrod[3]

Taxonomic Notes

Varieties: S. altissima var. altissima; S. altissima var. pluricephala;[1][2] S. altissima var. gilvocanescens;[1] S. altissima var. procera[2]
Synonym(s): S. canadensis var. scabra; S. hirsutissima;[1][2] S. pruinosa; S. canadensis var. gilvocanescens;[1] S. lunellii[2]

Description

Solidago altissima is a dioecious perennial forb/herb.[2] This plant is rough, erect, and produces small yellow flowers that are arranged along upper side of branches, producing a plume.[4] Each ramet contains 20,000 flowers on average.[5] It reaches heights of 3-6 ft (0.91-1.83 m)[3] and forms large compact below-ground rhizome systems.[4] Seeds averaged 42.9 µg.[5]

Distribution

This species is found in all of the lower 48 United States, excluding Washington, Oregon, Nevada, Utah, Idaho, and Wyoming. It also occurs in the Canadian provinces of Saskatchewan, Manitoba, Ontario, Quebec, and New Brunswick.[2] S. altissima is also an exotic invasive in Europe (as cited in [4]).

Ecology

Habitat

S. altissima is found in roadsides,[1][3] fields, disturbed areas,[1] thickets, prairies, open woods,[3] stream banks, and marshes.[6] It prefers moist to dry soils composed of clay, clay loam, medium loam, sandy loam, sandy and caliche.[3] In a Wisconsin Prairie, the frequency in 1951 was 32 and in 1961 was 48.[7] Also on Wisconsin prairies, aboveground biomass from 1987-1993 averaged 838.4 ± 92.8 g m-2 and mean percent cover ranging from 14.2-29.3% depending upon the fire regime.[8]

Phenology

Flowering occurs from August through November.[1][9]

Seed dispersal

Initial colonization occurs from seeds producing genets. Once established, increases within the population should occur via the production of ramets (clonal growth) according to a model.[10]

Seed bank and germination

Seed set of S. altissima was 22-25.2% in a study by the University of Kentucky. Another study in Kalamazoo County, Michigan in 1980 displayed a similar seed set of 33.2%, but showed this was higher late-flowering compared to early flowering clones.[5]

Fire ecology

On a Wisconsin tallgrass prairie, two burn cycles of a 3 year interval showed increases in cover during spring and summer burns. However, an increase in cover also occurred on unburned sites, suggesting the burn cycle did not negatively affect S. altissima cover but may not be responsible for the increase.[8]

Pollination

S. altissima attracts birds, butterflies, and a large number of native bees.[3] This includes non-native honey bees.[3][5]

Use by animals

S. altissima responds to insect herbivory by spending energy to maintain itself, rather than producing seeds.[11] There are at least 103 species of insect herbivores of S. altissima, 42 (from 17 families) are specialists on Solidagospp.[12]

Conservation and Management

Mowing does not effect the growth, survival, or reproduction of juvenile or seedling plants.[4]

Cultivation and restoration

Photo Gallery

References and notes

  1. 1.0 1.1 1.2 1.3 1.4 1.5 1.6 1.7 Weakley AS (2015) Flora of the Southern and Mid-Atlantic States. Chapel Hill, NC: University of North Carolina Herbarium.
  2. 2.0 2.1 2.2 2.3 2.4 2.5 2.6 USDA NRCS (2016) The PLANTS Database (http://plants.usda.gov, 118 January 2018). National Plant Data Team, Greensboro, NC 27401-4901 USA.
  3. 3.0 3.1 3.2 3.3 3.4 3.5 3.6 Plant database: Solidago altissima. (18 January 2018) Lady Bird Johnson Wildflower Center. URL: https://www.wildflower.org/plants/result.php?id_plant=SOAL6
  4. 4.0 4.1 4.2 4.3 Meyer AH, Schmid B (1999) Experimental demography of rhizome populations of establishing clones of Solidago altissima. Journal of Ecology 87(1):42-54. Cite error: Invalid <ref> tag; name "Meyer & Schmid 1999" defined multiple times with different content
  5. 5.0 5.1 5.2 5.3 Gross RS, Werner PA (1983) Relationships among flowering phenology, insect visitors, and seed-set of individuals: Experimental studies on four co-occurring species of goldenrod (Solidago: compositae). Ecological monographs 53(1):95-117.
  6. Bostick PE (1971) Vascular plants of Panola Mountain, Georgia. Castanea 36(3):194-209.
  7. Anderson RC (1973) The use of fire as a management tool on the Curtis Prairie. Proceedings Annual [12th] Tall Timbers Fire Ecology Conference: a quest for ecological understanding. Lubbock, TX pg 23-35.
  8. 8.0 8.1 Howe HF (1995) Succession and fire season in experimental prairie plantings. Ecology 76(6):1917-1925.
  9. Nelson G (18 January 2018) PanFlora. Retrieved from gilnelson.com/PanFlora/
  10. Eriksson O (1993) Dynamics of genets in clonal plants. Trends in Ecology and Evolution. 8(9):313-316.
  11. Root RB (1996) Herbivore pressure on goldenrods (Solidago altissima): Its variation and cumulative effects. Ecology 77(4):1074-1087.
  12. Root RB & Cappuccino N (1992) Patterns in population change and the organization of the insect community associated with goldenrod. Ecological Monographs 62(3):393-420.