Print Report
A4150 Sequoiadendron giganteum Forest Alliance
Type Concept Sentence: This alliance consists of mixed conifer forests where Sequoiadendron giganteum is the dominant or at least characteristic tree, usually with other trees such as Abies lowiana, Calocedrus decurrens, Quercus kelloggii, Pseudotsuga menziesii, Pinus jeffreyi, Pinus ponderosa, and/or Pinus lambertiana. This forest alliance occurs along the western slope of California''s Sierra Nevada.
Common (Translated Scientific) Name: Giant Sequoia Forest Alliance
Colloquial Name: Giant Sequoia Forest
Hierarchy Level: Alliance
Type Concept: This alliance consists of mixed conifer forest where Sequoiadendron giganteum is the dominant or at least characteristic tree within the stand. Other trees present in the canopy include Abies lowiana, Calocedrus decurrens, Abies magnifica, Quercus kelloggii, Pseudotsuga menziesii, Pinus jeffreyi, Pinus contorta var. murrayana, Pinus ponderosa, and/or Pinus lambertiana. Shrubs may be infrequent to common and include Chrysolepis sempervirens, Chamaebatia foliolosa, Ceanothus spp., Arctostaphylos patula, Rhododendron occidentale, Ribes spp., Rosa spp., and Rubus spp. Stand structure and composition vary considerably with elevation, latitude, exposure, soil moisture, and time since most recent fire or disturbance. This forest alliance occurs along the western slope of California''s Sierra Nevada.
Diagnostic Characteristics: Diagnostic of this forest alliance is the presence of large Sequoiadendron giganteum in the upper tree canopy.
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: This alliance is based on Sawyer et al. (2009) Sequoiadendron giganteum Forest Alliance where Sequoiadendron giganteum is dispersed throughout the stand or is an emergent with >10% absolute canopy cover.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: Tall conifer trees (>70 m tall) dominate the canopy. Mixed conifers are often interspersed within groves forming a subcanopy. Shrubs are infrequent to common; the herbaceous layer is sparse to abundant.
Floristics: This forest alliance is characterized by the presence of Sequoiadendron giganteum. Other dominant trees include Quercus kelloggii, Pseudotsuga menziesii, Calocedrus decurrens (= Libocedrus decurrens), Pinus jeffreyi, Pinus contorta var. murrayana, Pinus ponderosa, Abies magnifica, Pinus lambertiana, and Abies lowiana (= Abies concolor var. lowiana). Groves can have a canopy of Abies lowiana with emergent individuals of Sequoiadendron giganteum. At lower elevations Calocedrus decurrens may dominate and at higher elevations Abies magnifica may dominate. Shrubs may be infrequent to common, and may include Chrysolepis sempervirens (= Castanopsis sempervirens), Chamaebatia foliolosa, Ceanothus cordulatus, Ceanothus parvifolius, Ceanothus integerrimus, Ceanothus velutinus, Arctostaphylos patula, Rhododendron occidentale, Ribes spp., Rosa spp., and Rubus spp. Stand structure varies considerably with elevation, latitude, exposure, soil moisture, and time since most recent fire or disturbance.
Dynamics: Fire is the most important agent in the maintenance of this forest alliance. As a species, sequoias are very shade-intolerant and require openings within the forest canopy to establish. The species'' optimal habitat is mesic sites with good soils, and disturbance is required to open up areas with such favorable conditions. Fire reduces light competition, and increases the friability and the wetability of the exposed surface mineral soils. These are exactly the conditions most conducive to germination and establishment of sequoia seedlings. The survival rate for sequoia seedlings has been found to be 27% following a hot fire. No seedlings survived in adjacent, undisturbed areas. Fires within established groves are the single largest agent of seed drop. Heat from the fire convects into the canopy, drying and opening the mature seed cones. This allows up to 8,000,000 seeds/acre to drop. This seed drop corresponds to the favorable seed bed conditions created by the fire. Sequoia seeds are very light (91,000/lb) and winged. The updrafts caused by fire or the winds typical of the Sierra Nevada can disperse seeds more than a 1/2 mile. Once established, sequoias maintain dominance by rapid growth. Young sequoias are very susceptible to injury or death by fire, but because they usually germinate in areas recently burned, they often are large enough to withstand a light fire by the time the fuel loads would allow one to occur. Large sequoias are very fire-resistant due to their thick, non-resinous bark and elevated crowns. Few mature sequoias are killed directly by fire. Repeated fires can eventually sear through the bark near the tree base, kill underlying cambium, and produce an ever-enlarging scar. These scars provide entry points for insects and fungi, which weaken the tree. Most sequoias are killed by toppling, with a significant percentage of trees failing at the point of greatest insect and/or fungi damage and falling to the fire-scarred side. Fire suppression during the 20th century has caused a massive failure in sequoia regeneration. The reduced fire frequency also allows greater litter accumulation, increasing the severity of fires when they do occur.
Environmental Description: Sequoiadendron giganteum is limited by temperature in the upper elevations, and by deficient soil moisture at lower elevations. Elevations typically range from 825-2700 m. Groves in the northern portion of the range tend to occur on southern aspects; those in the southern portion tend to occur on northern aspects. Most groves occur on granitic-based residual soils, alluvium or glacial outwash. Sequoias grow best in deep, well-drained, sandy loams with perennial soil moisture. Vigorous individuals can thrive in shallow, rocky soils if underground water is available. Soil moisture seems to be the limiting factor in the extent of a grove or stand of sequoias. Most groves occur on granitic-based residual soils, alluviums, or glacial outwash.
Geographic Range: Groves of giant sequoia are scattered in a belt about 24 km wide and 420 km long on the west slope of California''s Sierra Nevada.
Nations: US
States/Provinces: CA
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.935195
Confidence Level: Low
Confidence Level Comments: No Data Available
Grank: GNR
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 1 Forest & Woodland Class | C01 | 1 |
Subclass | 1.B Temperate & Boreal Forest & Woodland Subclass | S15 | 1.B |
Formation | 1.B.2 Cool Temperate Forest & Woodland Formation | F008 | 1.B.2 |
Division | 1.B.2.Nd Vancouverian Forest & Woodland Division | D192 | 1.B.2.Nd |
Macrogroup | 1.B.2.Nd.2 Incense-cedar - Jeffrey Pine - Sierra White Fir Forest Macrogroup | M023 | 1.B.2.Nd.2 |
Group | 1.B.2.Nd.2.a Incense-cedar - Sugar Pine - Sierra White Fir Forest & Woodland Group | G344 | 1.B.2.Nd.2.a |
Alliance | A4150 Giant Sequoia Forest Alliance | A4150 | 1.B.2.Nd.2.a |
Association | CEGL003108 Giant Sequoia Forest | CEGL003108 | 1.B.2.Nd.2.a |
Association | CEGL008607 Giant Sequoia - Sugar Pine / Pacific Dogwood Forest | CEGL008607 | 1.B.2.Nd.2.a |
Concept Lineage: A.101
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: = Sequoiadendron giganteum (Giant sequoia forest) Alliance (Sawyer et al. 2009) [86.200.00]
= Sequoiadendron giganteum Forest Alliance (CNPS 2017) [86.200.00]
= Big Tree Forest (#84250) (Holland 1986b) [This synonym was used by Robert Holland and is widely quoted in literature.]
= Giant Sequoia Series (Sawyer and Keeler-Wolf 1995) [This name is a synonym for the alliance used by the California Heritage Division.]
? Sierra Nevada Mixed Conifer type-SAF (Burns and Honkala 1990a) [Giant sequoia groves lie entirely within this Society of American Foresters cover type 243.]
= Sequoiadendron giganteum Forest Alliance (CNPS 2017) [86.200.00]
= Big Tree Forest (#84250) (Holland 1986b) [This synonym was used by Robert Holland and is widely quoted in literature.]
= Giant Sequoia Series (Sawyer and Keeler-Wolf 1995) [This name is a synonym for the alliance used by the California Heritage Division.]
? Sierra Nevada Mixed Conifer type-SAF (Burns and Honkala 1990a) [Giant sequoia groves lie entirely within this Society of American Foresters cover type 243.]
- Aune, P. S., technical coordinator. 1994. Proceedings of the Symposium on Giant Sequoias: Their place in the ecosystem and society. 1992 June 23-25, Visalia, CA. General Technical Report PSW-GTR-151. USDA Forest Service, Pacific and Southwestern Research Station, Visalia, CA. 170 pp.
- Barbour, M. G. 1988. Californian upland forests and woodlands. Pages 131-164 in: M. G. Barbour and W. D. Billings, editors. North American terrestrial vegetation. Cambridge University Press, New York, NY.
- Barbour, M. G., T. C. Wainwright, and C. Manansala. 1981. Preparation of a vegetation map of Calaveras Big Trees State Park. Unpublished report. State of California, The Resources Agency, Department of Parks and Recreation, Sacramento, CA.
- Biswell, H. H., H. Buchanan, and R. P. Gibbens. 1966. Ecology of the vegetation of a second-growth sequoia forest. Ecology 47:630-633.
- Burns, R. M., and B. H. Honkala, technical coordinators. 1990a. Silvics of North America: Volume 1. Conifers. Agriculture Handbook 654. USDA Forest Service, Washington, DC. 675 pp.
- CNPS [California Native Plant Society]. 2015-2017. A manual of California vegetation [online]. California Native Plant Society, Sacramento, CA. [http://vegetation.cnps.org/].
- Conard, S. G., and S. R. Radosevich. 1982. Post-fire succession in white fir (Abies concolor) vegetation of the northern Sierra Nevada. Madrono 29(1):42-56.
- Eyre, F. H., editor. 1980. Forest cover types of the United States and Canada. Society of American Foresters, Washington, DC. 148 pp.
- Faber-Langendoen, D., J. Drake, M. Hall, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, M. Russo, K. Schulz, L. Sneddon, K. Snow, and J. Teague. 2013-2019b. Screening alliances for induction into the U.S. National Vegetation Classification: Part 1 - Alliance concept review. NatureServe, Arlington, VA.
- Fites-Kaufman, J. A., P. Rundel, N. Stephenson, and D. A. Weixelman. 2007. Montane and subalpine vegetation of the Sierra Nevada and Cascade ranges. Pages 456-501 in: M. Barbour, T. Keeler-Wolf, and A. A. Schoenherr, editors. Terrestrial Vegetation of California, third edition. University of California Press, Berkeley.
- Griffin, J. R., and W. B. Critchfield. 1976. The distribution of forest trees in California. Research Paper PSW-82. USDA Forest Service, Pacific Southwest Forest and Range Experiment Station, Berkeley, CA. 115 pp.
- Habeck, R. J. 1992c. Sequoiadendron giganteum. In: Fire Effects Information System [Online]. USDA Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). [http://www.fs.fed.us/database/feis/]
- Holland, R. F. 1986b. Preliminary descriptions of the terrestrial natural communities of California. Unpublished report prepared for the California Department of Fish and Game, Nongame-Heritage Program and Natural Diversity Database, Sacramento. 156 pp.
- Johnston, B. C. 1984. Plant associations of Region Two. Edition 3.5. USDA Forest Service, Rocky Mountain Region. Lakewood, CO.
- Keeler-Wolf, T., M. Schindel, S. San, P. Moore, and D. Hickson. 2003a. Classification of the vegetation of Yosemite National Park and surrounding environs in Tuolumne, Mariposa, Madera and Mono counties, California. Unpublished report by NatureServe in cooperation with the California Native Plant Society and California Department of Fish and Game, Wildlife and Habitat Data Analysis Branch, Sacramento, CA.
- Kilgore, B. M., and D. Taylor. 1979. Fire history of a Sequoia-mixed conifer forest. Ecology 60:129-142.
- Küchler, A. W. 1964. Potential natural vegetation of the conterminous United States. American Geographic Society Special Publication 36. New York, NY. 116 pp.
- Nichols, H. T. 1989. Managing fire in Sequoia and Kings Canyon national parks. Fremontia 16:11-14.
- Rundel, P. W. 1971. Community structure and stability in the giant sequoia groves of the Sierra Nevada, California. American Midland Naturalist 84:478-492.
- Rundel, P. W. 1972a. An annotated checklist of the groves of Sequoiadendron giganteum in the Sierra Nevada, California. Madroño 21:319-383.
- Rundel, P. W. 1972b. Habitat restriction in giant sequoia: The environmental control of grove boundaries. American Midland Naturalist 87:81-99.
- Rundel, P. W., D. J. Parsons, and D. T. Gordon. 1977. Montane and subalpine vegetation of the Sierra Nevada and Cascade Ranges. Pages 559-599 in: M. G. Barbour and J. Major, editors. Terrestrial vegetation of California. Wiley-Interscience, reprinted 1988 by the California Native Plant Society, Sacramento, CA.
- Sawyer, J. O., T. Keeler-Wolf, and J. Evens. 2009. A manual of California vegetation. Second edition. California Native Plant Society, Sacramento CA. 1300 pp.
- Sawyer, J. O., and T. Keeler-Wolf. 1995. A manual of California vegetation. California Native Plant Society, Sacramento. 471 pp.
- Weatherspoon, C. P. 1990. Sequoiadendron giganteum, giant sequoia. Pages 552-562 in: R. M. Burns and B. H. Honkala, editors. Silvics of North America, Volume 1: conifers. Agriculture Handbook 654. USDA Forest Service, Washington, DC.
- Willard, D. 2000. A guide to the sequoia groves of California. Yosemite Association. Yosemite National Park, CA.
- van Wagtendonk, J. W., and J. Fites-Kauffman. 2006. Sierra Nevada bioregion. Pages 264-294 in: N. G. Sugihara, J. W. van Wagtendonk, K. E. Shaffer, J. Fites-Kaufman, and A. E. Thode, editors. Fire in California''s ecosystems. University of California Press, Berkeley, CA.