Difference between revisions of "Solidago altissima"
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==Taxonomic Notes== | ==Taxonomic Notes== | ||
| − | + | Synonym(s): ''S. canadensis'' var. ''scabra''; ''S. hirsutissima''; ''S. pruinosa''; ''S. canadensis'' var. ''gilvocanescens'' | |
| − | + | ||
| + | Varieties: ''S. altissima'' Linnaeus var. ''altissima''; ''S. altissima'' Linnaeus var. ''pluricephala (Rydberg) Semple''; ''S. altissima'' Linnaeus var. ''gilvocanescens'' M.C. Johnston | ||
==Description== <!-- Basic life history facts such as annual/perrenial, monoecious/dioecious, root morphology, seed type, etc. --> | ==Description== <!-- Basic life history facts such as annual/perrenial, monoecious/dioecious, root morphology, seed type, etc. --> | ||
| − | ''Solidago altissima'' is a dioecious perennial forb/herb.<ref name="USDA"/> This plant is rough, erect, and produces small yellow flowers that are arranged along upper side of branches, producing a plume. It reaches heights of 3-6 ft (0.91-1.83 m)<ref name="Ladybird"/> and forms large compact below-ground rhizome systems.<ref name="Meyer & Schmid | + | ''Solidago altissima'' is a dioecious perennial forb/herb.<ref name="USDA"/> This plant is rough, erect, and produces small yellow flowers that are arranged along upper side of branches, producing a plume.<ref name="Meyer & Schmid 1999b"/> Each ramet contains 20,000 flowers on average.<ref name="Gross & Werner 1983">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.</ref> It reaches heights of 3-6 ft (0.91-1.83 m)<ref name="Ladybird"/> and forms large compact below-ground rhizome systems.<ref name="Meyer & Schmid 1999b">Meyer AH, Schmid B (1999) Experimental demography of rhizome populations of establishing clones of ''Solidago altissima''. Journal of Ecology 87(1):42-54.</ref> Seeds averaged 42.9 µg.<ref name="Gross & Werner 1983"/> |
==Distribution== | ==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.<ref name="USDA"/> ''S. altissima'' is also an exotic invasive in Europe (as cited in <ref name="Meyer & Schmid 1999">Meyer AH, Schmid B (1999) Experimental demography of old-field perennial solidago altissima: The dynamics of the shoot population. Journal of Ecology 87(1):17-27.</ref>). | + | 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.<ref name="USDA"/> ''S. altissima'' is also an exotic invasive in Europe (as cited in<ref name="Meyer & Schmid 1999">Meyer AH, Schmid B (1999) Experimental demography of old-field perennial solidago altissima: The dynamics of the shoot population. Journal of Ecology 87(1):17-27.</ref>). |
==Ecology== | ==Ecology== | ||
===Habitat=== <!--Natural communities, human disturbed habitats, topography, hydrology, soils, light, fire regime requirements for removal of competition, etc.--> | ===Habitat=== <!--Natural communities, human disturbed habitats, topography, hydrology, soils, light, fire regime requirements for removal of competition, etc.--> | ||
| − | ''S. altissima'' is found in | + | ''S. altissima'' is found in thickets, prairies, open woods,<ref name="Ladybird"/> stream banks, limestone glades, sand pine ridges, pond shores, live oak groves, floodplain forests, and marshes.<ref name="Bostick 1971">Bostick PE (1971) Vascular plants of Panola Mountain, Georgia. Castanea 36(3):194-209.</ref><ref name="FSU"> Florida State University Herbarium Database. URL: http://herbarium.bio.fsu.edu. Last accessed: June 2021. Collectors: Loran C. Anderson, K. Craddock Burks, A. F. Clewell, R.K. Godfrey, Bruce Hansen, JoAnn Hansen, and R. Kral. States and counties: Florida: Dixie, Escambia, Franklin, Gadsden, Jackson, Jefferson, Leon, and Walton.</ref> It is also found in disturbed areas including under highway bridges, fields, roadsides, ditches, burned pinelands, and woodland remnants.<ref name="FSU"/> |
| + | |||
| + | This species prefers moist to dry soils composed of clay, clay loam, medium loam, sandy loam, sandy and caliche.<ref name="Ladybird"/> In a Wisconsin Prairie, the frequency in 1951 was 32 and in 1961 was 48.<ref name="Anderson 1973">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.</ref> Also on Wisconsin prairies, aboveground biomass from 1987-1993 averaged 838.4 ± 92.8 g m<sup>-2</sup> and mean percent cover ranging from 14.2-29.3% depending upon the fire regime.<ref name="Howe 1995"/> | ||
| + | ''S. altissima'' responded positively to soil disturbance by agriculture in Southwest Georgia.<ref>Hedman, C.W., S.L. Grace, and S.E. King. (2000). Vegetation composition and structure of southern coastal plain pine forests: an ecological comparison. Forest Ecology and Management 134:233-247.</ref> | ||
| + | |||
| + | Associated species: ''Schoenus nigricans, Aristida spp., Muhlenbergia, Serenoa repens, Pinus clausa, Heterotheca'', and ''Juniperus''.<ref name="FSU"/> | ||
===Phenology=== <!--Timing off flowering, fruiting, seed dispersal, and environmental triggers. Cite PanFlora website if appropriate: http://www.gilnelson.com/PanFlora/ --> | ===Phenology=== <!--Timing off flowering, fruiting, seed dispersal, and environmental triggers. Cite PanFlora website if appropriate: http://www.gilnelson.com/PanFlora/ --> | ||
| − | + | ''S. altissima'' has been observed flowering from August through November.<ref name="Weakley 2015"/><ref name="PanFlora">Nelson, G. PanFlora: Plant data for the eastern United States with emphasis on the Southeastern Coastal Plains, Florida, and the Florida Panhandle. www.gilnelson.com/PanFlora/ Accessed: 18 JAN 2018</ref> | |
| − | + | ||
| − | + | ===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.<ref name="Eriksson 1993">Eriksson O (1993) Dynamics of genets in clonal plants. Trends in Ecology and Evolution. 8(9):313-316.</ref> | |
| + | |||
| + | ===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.<ref name="Gross & Werner 1983"/> | ||
| + | |||
| + | ===Fire ecology=== <!--Fire tolerance, fire dependence, adaptive fire responses--> | ||
| + | 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.<ref name="Howe 1995">Howe HF (1995) Succession and fire season in experimental prairie plantings. Ecology 76(6):1917-1925.</ref> | ||
| + | |||
| + | Populations of ''Solidago altissima'' have been known to persist through repeated annual burns.<ref>Robertson, K.M. Unpublished data collected from Pebble Hill Fire Plots, Pebble Hill Plantation, Thomasville, Georgia.</ref><ref>Glitzenstein, J. S., D. R. Streng, R. E. Masters, K. M. Robertson and S. M. Hermann 2012. Fire-frequency effects on vegetation in north Florida pinelands: Another look at the long-term Stoddard Fire Research Plots at Tall Timbers Research Station. Forest Ecology and Management 264: 197-209.</ref><ref>Platt, W.J., R. Carter, G. Nelson, W. Baker, S. Hermann, J. Kane, L. Anderson, M. Smith, K. Robertson. 2021. Unpublished species list of Wade Tract old-growth longleaf pine savanna, Thomasville, Georgia.</ref> | ||
| − | ===Pollination=== | + | ===Pollination=== |
| − | ''S. altissima'' attracts birds, butterflies, and a large number of native bees.<ref name="Ladybird"/> | + | ''S. altissima'' is visited by ground-nesting bees from the Andrenidae family (''Andrena hirticincta, A. nubecula'' and ''Perdita octomaculata''), long-tongued bees from the Apidae family (''Bombus impatiens'' and ''Melissodes druriella''), leaf beetles from the Chrysomelidae family such as ''Diabrotica undecimpunctata'', sweat bees from the Halictidae family such as ''Lasioglossum lineatulum'', butterflies from the Nymphalidae family such as ''Danaus plexippus'' and assassin bugs from the Reduviidae family such as ''Phymata americana''.<ref>Discoverlife.org [https://www.discoverlife.org/20/q?search=Bidens+albaDiscoverlife.org|Discoverlife.org]</ref> ''S. altissima'' attracts birds, butterflies, and a large number of native bees.<ref name="Ladybird"/> This includes non-native honey bees.<ref name="Ladybird"/><ref name="Gross & Werner 1983"/> |
| − | === | + | ===Herbivory and toxicology===<!--Common herbivores, granivory, insect hosting, poisonous chemicals, allelopathy, etc--> |
| − | ''S. altissima'' responds to insect herbivory by spending energy to maintain itself, rather than producing seeds.<ref name="Root 1996">Root RB (1996) Herbivore pressure on goldenrods (''Solidago altissima''): Its variation and cumulative effects. Ecology 77(4):1074-1087.</ref> There are at least 103 species of insect herbivores of ''S. altissima'', 42 (from 17 families) are specialists on ''Solidago'' | + | ''S. altissima'' responds to insect herbivory by spending energy to maintain itself, rather than producing seeds.<ref name="Root 1996">Root RB (1996) Herbivore pressure on goldenrods (''Solidago altissima''): Its variation and cumulative effects. Ecology 77(4):1074-1087.</ref> There are at least 103 species of insect herbivores of ''S. altissima'', 42 (from 17 families) are specialists on genus ''Solidago''.<ref name="Root & Cappuccino 1992">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.</ref> |
<!--==Diseases and parasites==--> | <!--==Diseases and parasites==--> | ||
| − | ==Conservation and | + | ==Conservation, cultivation, and restoration== |
| + | Mowing does not effect the growth, survival, or reproduction of juvenile or seedling plants.<ref name="Meyer & Schmid 1999a">Meyer AH, Schmid B (1999) Seed dynamics and seedling establishment in the invading perennial ''Solidago altissima'' under different experimental treatments. Journal of Ecology 87:28-41.</ref> | ||
| + | |||
| + | ==Cultural use== | ||
| − | |||
==Photo Gallery== | ==Photo Gallery== | ||
<gallery widths=180px> | <gallery widths=180px> | ||
</gallery> | </gallery> | ||
==References and notes== | ==References and notes== | ||
Latest revision as of 12:15, 15 July 2022
| Solidago altissima | |
|---|---|
| |
| 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. | |
| |
| 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]
Contents
Taxonomic Notes
Synonym(s): S. canadensis var. scabra; S. hirsutissima; S. pruinosa; S. canadensis var. gilvocanescens
Varieties: S. altissima Linnaeus var. altissima; S. altissima Linnaeus var. pluricephala (Rydberg) Semple; S. altissima Linnaeus var. gilvocanescens M.C. Johnston
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[6]).
Ecology
Habitat
S. altissima is found in thickets, prairies, open woods,[3] stream banks, limestone glades, sand pine ridges, pond shores, live oak groves, floodplain forests, and marshes.[7][8] It is also found in disturbed areas including under highway bridges, fields, roadsides, ditches, burned pinelands, and woodland remnants.[8]
This species 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.[9] 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.[10] S. altissima responded positively to soil disturbance by agriculture in Southwest Georgia.[11]
Associated species: Schoenus nigricans, Aristida spp., Muhlenbergia, Serenoa repens, Pinus clausa, Heterotheca, and Juniperus.[8]
Phenology
S. altissima has been observed flowering from August through November.[1][12]
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.[13]
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.[10]
Populations of Solidago altissima have been known to persist through repeated annual burns.[14][15][16]
Pollination
S. altissima is visited by ground-nesting bees from the Andrenidae family (Andrena hirticincta, A. nubecula and Perdita octomaculata), long-tongued bees from the Apidae family (Bombus impatiens and Melissodes druriella), leaf beetles from the Chrysomelidae family such as Diabrotica undecimpunctata, sweat bees from the Halictidae family such as Lasioglossum lineatulum, butterflies from the Nymphalidae family such as Danaus plexippus and assassin bugs from the Reduviidae family such as Phymata americana.[17] S. altissima attracts birds, butterflies, and a large number of native bees.[3] This includes non-native honey bees.[3][5]
Herbivory and toxicology
S. altissima responds to insect herbivory by spending energy to maintain itself, rather than producing seeds.[18] There are at least 103 species of insect herbivores of S. altissima, 42 (from 17 families) are specialists on genus Solidago.[19]
Conservation, cultivation, and restoration
Mowing does not effect the growth, survival, or reproduction of juvenile or seedling plants.[20]
Cultural use
Photo Gallery
References and notes
- ↑ 1.0 1.1 Weakley AS (2015) Flora of the Southern and Mid-Atlantic States. Chapel Hill, NC: University of North Carolina Herbarium.
- ↑ 2.0 2.1 2.2 USDA NRCS (2016) The PLANTS Database (http://plants.usda.gov, 118 January 2018). National Plant Data Team, Greensboro, NC 27401-4901 USA.
- ↑ 3.0 3.1 3.2 3.3 3.4 3.5 Plant database: Solidago altissima. (18 January 2018) Lady Bird Johnson Wildflower Center. URL: https://www.wildflower.org/plants/result.php?id_plant=SOAL6
- ↑ 4.0 4.1 Meyer AH, Schmid B (1999) Experimental demography of rhizome populations of establishing clones of Solidago altissima. Journal of Ecology 87(1):42-54.
- ↑ 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.
- ↑ Meyer AH, Schmid B (1999) Experimental demography of old-field perennial solidago altissima: The dynamics of the shoot population. Journal of Ecology 87(1):17-27.
- ↑ Bostick PE (1971) Vascular plants of Panola Mountain, Georgia. Castanea 36(3):194-209.
- ↑ 8.0 8.1 8.2 Florida State University Herbarium Database. URL: http://herbarium.bio.fsu.edu. Last accessed: June 2021. Collectors: Loran C. Anderson, K. Craddock Burks, A. F. Clewell, R.K. Godfrey, Bruce Hansen, JoAnn Hansen, and R. Kral. States and counties: Florida: Dixie, Escambia, Franklin, Gadsden, Jackson, Jefferson, Leon, and Walton.
- ↑ 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.
- ↑ 10.0 10.1 Howe HF (1995) Succession and fire season in experimental prairie plantings. Ecology 76(6):1917-1925.
- ↑ Hedman, C.W., S.L. Grace, and S.E. King. (2000). Vegetation composition and structure of southern coastal plain pine forests: an ecological comparison. Forest Ecology and Management 134:233-247.
- ↑ Nelson, G. PanFlora: Plant data for the eastern United States with emphasis on the Southeastern Coastal Plains, Florida, and the Florida Panhandle. www.gilnelson.com/PanFlora/ Accessed: 18 JAN 2018
- ↑ Eriksson O (1993) Dynamics of genets in clonal plants. Trends in Ecology and Evolution. 8(9):313-316.
- ↑ Robertson, K.M. Unpublished data collected from Pebble Hill Fire Plots, Pebble Hill Plantation, Thomasville, Georgia.
- ↑ Glitzenstein, J. S., D. R. Streng, R. E. Masters, K. M. Robertson and S. M. Hermann 2012. Fire-frequency effects on vegetation in north Florida pinelands: Another look at the long-term Stoddard Fire Research Plots at Tall Timbers Research Station. Forest Ecology and Management 264: 197-209.
- ↑ Platt, W.J., R. Carter, G. Nelson, W. Baker, S. Hermann, J. Kane, L. Anderson, M. Smith, K. Robertson. 2021. Unpublished species list of Wade Tract old-growth longleaf pine savanna, Thomasville, Georgia.
- ↑ Discoverlife.org [1]
- ↑ Root RB (1996) Herbivore pressure on goldenrods (Solidago altissima): Its variation and cumulative effects. Ecology 77(4):1074-1087.
- ↑ 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.
- ↑ Meyer AH, Schmid B (1999) Seed dynamics and seedling establishment in the invading perennial Solidago altissima under different experimental treatments. Journal of Ecology 87:28-41.
