The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T34023A2840676 Sequoiadendron giganteum, Giant Sequoia Assessment by: Schmid, R. & Farjon, A. View on www.iucnredlist.org Citation: Schmid, R. & Farjon, A. 2013. Sequoiadendron giganteum. The IUCN Red List of Threatened Species 2013: e.T34023A2840676. http://dx.doi.org/10.2305/IUCN.UK.20131.RLTS.T34023A2840676.en Copyright: © 2015 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written permission from the copyright holder. For further details see Terms of Use. The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: BirdLife International; Botanic Gardens Conservation International; Conservation International; Microsoft; NatureServe; Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; Wildscreen; and Zoological Society of London. If you see any errors or have any questions or suggestions on what is shown in this document, please provide us with feedback so that we can correct or extend the information provided. THE IUCN RED LIST OF THREATENED SPECIES™ Taxonomy Kingdom Phylum Class Order Family Plantae Tracheophyta Pinopsida Pinales Cupressaceae Taxon Name: Sequoiadendron giganteum (Lindl.) J.T.Buchholz Synonym(s): • Wellingtonia gigantea Lindl. Common Name(s): • English: Giant Sequoia, Bigtree, Sequoia, Sierra Redwood Taxonomic Source(s): Farjon, A. 2010. A Handbook of the World's Conifers. Koninklijke Brill, Leiden. Taxonomic Notes: This species was formerly included under the family Taxodiaceae. That family is now merged with Cupressaceae (see Farjon 2005). Assessment Information Red List Category & Criteria: Endangered B2ab(ii,iii,v) ver 3.1 Year Published: 2013 Date Assessed: April 18, 2011 Justification: Despite the fact that almost all existing ‘groves’ of Sequoiadendron giganteum are in protected areas and some have been protected for more than a century, the population is in continuous decline. The actual area of occupancy, estimated to be 142 km2, falls well below the threshold for Endangered (500 km²) and with a continuing decline due to inadequate regeneration and natural death of (over)mature trees, which are being replaced by other, competing conifers, the B2 criterion applies and the species meets the criteria for listing as Endangered. Previously Published Red List Assessments 1998 – Vulnerable (VU) 1998 – Vulnerable (V) Geographic Range Range Description: Endemic to the USA: California, Sierra Nevada (Calaveras, Fresno, Madera, Mariposa, Placer, Tulare & Tuolumne Counties). It is known to occur in ca. 67 groves which stretch over a length of ca. 400 km along the western slopes of the Sierra Nevada in a belt at most 25 km wide (severely fragmented), © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 1 covering a total area of occupancy of ca. 14,200 ha. Most of the groves (59) are in the two southernmost counties: Fresno and Tulare. Country Occurrence: Native: United States (California) © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 2 Population The present trend in recruitment of Sequoiadendron giganteum is downwards, due to competition in the absence of periodic fires in many of the protected groves. This leads over time to a downward trend in the number of mature individuals in the population. There is at present insufficient regeneration to maintain Sequoia populations in these groves (Stephenson in Aune1992, Stephenson 1996). Current Population Trend: Decreasing Habitat and Ecology (see Appendix for additional information) This species is forming 'groves' of a few to over 20,000 individuals in the Mixed Conifer Forest belt on the western slopes of the Sierra Nevada. It is mixed with other conifers: Abies concolor, A. magnifica, Calocedrus decurrens, Pinus lambertiana, P. ponderosa, P. jeffreyi, Pseudotsuga menziesii, Taxus brevifolia, and with fewer broad-leaved trees: Quercus kelloggii, Q. chrysolepis, Cornus nuttallii, Alnus rhombifolia, Salix scoulerana, Acer macrophyllum, and shrubs: Castanopsis sempervirens, Ceanothus cordulatus, C. parvifolius, C. integerrimus, Arctostaphylos patula, etc. The relatively narrow altitudinal belt, (830-)1,400-2,150(-2,700) m a.s.l., and the scattered concentration of groves, which tend to become smaller and further apart going north, indicate rather narrow climatic and soil conditions that are optimal in its natural habitat. Most groves are on granite-based residual and alluvial soils, some on glacial outwash, and mildly acidic; best growth is on deep, well-drained sandy loams with available ground water, the latter appears to be an important limiting factor. The climate is humid, with mostly autumn rain and winter snow, and dry summers, with mean annual precipitation between 900-1,400 mm, but with high year-to-year variation. Temperature in winter is mild, with light frosts but occasional extremes, and warm, occasionally hot, in summer. Sequoiadendron giganteum is well adapted to lowintensity forest fires (extremely thick bark) and resists windfall exceptionally well; its wood is also rotresistant. As a result its longevity ranges from 2,000-3,000(-3,200) years. Systems: Terrestrial Use and Trade (see Appendix for additional information) Since its discovery by Europeans in the mid-19th century, exploitation during the latter half of that century and into the next was considerable. The trees, though of high lumber quality and rot-resistant, often shattered on impact of the giant boles. What wood could be used was put into mainly building applications, and many larger houses in San Francisco and the Bay Area were built of its timber. No commercial exploitation of wild groves occurs at present, and most of these were protected for their scenic and scientific values many years ago. The giant trees are a major international tourist attraction in California. The Giant Sequoia is also highly regarded as an ornamental tree in parks and gardens of large homes and, being easily propagated from seed, is sold by many tree nurseries. Several cultivars have been named and are in the trade. The species also has potential as a managed-forest tree for timber production, but has found few applications in commercial forestry thus far. Threats (see Appendix for additional information) Although nearly all groves (or 92% of the area of occupancy) are on public land, enjoying various levels of protection, the species was previously listed as Vulnerable primarily because of historic rates of decline caused by exploitation. Present problems include fire risks, largely due to (past) management © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 3 practices which tended to benefit its coniferous competitors (especially Abies) rather than the target species, and which have greatly accumulated the fuel load for future fires to burn more devastatingly (Elliott-Fisk et al.1997). Crown fires could easily spread from adjacent stands of other conifers. Genetic integrity of the small northernmost (and isolated) grove in Placer County is jeopardized by nearby plantings of S. giganteum from other sources (Elliott-Fisk et al. 1997). Conservation Actions (see Appendix for additional information) Nearly all know ‘groves’ of this species are in protected areas; many are within famous national parks or within wilderness reserves of National Forests. There is a considerable literature on the conservation aspects of this species; for compilations see Aune (1994) and Stephenson (1996). The main conservation issue is the long absence of naturally occurring fires in the protected areas where many of the groves of Giant Sequoia occur. Different approaches to solve this problem, from controlled burning to selective logging, have been applied on different lands (burning in national parks, logging in national forests), but so far on too limited a scale to reverse the downward trend in recruitment necessary to maintain the population in the long term. More drastic measures seem to be needed, but are difficult to safely apply and/or are controversial (Elliott-Fisk et al. 1997). Credits Assessor(s): Schmid, R. & Farjon, A. Reviewer(s): Thomas, P. & Stritch, L. © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 4 Bibliography Aune, P.S. 1994. Proceedings of the symposium on Giant Sequoias: their place in the ecosystem and society, June 23-25, 1992. Gen. Tech. Report PSW-GTR-151. USDA Forest Service , Visalia, California. Burns, R.M. and Honkala, B.H. 1990. Silvics of North America. USDA, Forest Service, Washington, DC. Elliott-Fisk, D.L., Stephens, S.L., Aubert, J.E., Murphy, D. and Schaber, J. 1997. Mediated Settlement Agreement for Sequoia National Forest, Section B. Giant Sequoia Groves: an evaluation. Pp. 277-328 in SNEP Science Team and special consultants, Sierra Nevada Ecosystem Project: Final report to Congress: status of the Sierra Nevada. Wildland Resources Center report, no. 40. Centers for Water and Wildland Resources, University of California, Davis. Farjon, A. 2005. A Monograph of Cupressaceae and Sciadopitys. The Royal Botanic Gardens, Kew. Farjon, A. 2010. Conifer Database (June 2008) In Species 2000 & ITIS Catalogue of Life: 2010 Annual Checklist (Bisby F.A., Roskov Y.R., Orrell T.M., Nicolson D., Paglinawan L.E., Bailly N., Kirk P.M., Bourgoin T., Baillargeon G., eds). Reading, UK. Available at: http://www.catalogueoflife.org/. Farjon, A. 2010. A Handbook of the World's Conifers. Koninklijke Brill, Leiden. Hartesveldt, R.J., Harvey, H.T., Shellhammer, H.S. and Stecker, R.E. 1975. The Giant Sequoia of the Sierra Nevada. U.S. Dept. of the Interior, National Park Service, Washington, D.C. IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.1). Available at: http://www.iucnredlist.org. (Accessed: 12 June 2013). Stephenson, N.L. 1996. Giant sequoia management issues: protection, restoration, and conservation. SNEP Science Team and special consultants, Sierra Nevada Ecosystem Project: Final report to Congress: Status of the Sierra Nevada. Vol. 2. Assessments and scientific basis for management options. Centers for Water and Wildland Resources, University of California, Davis (series: Wildland Resources Center report, no. 37, pp. 1431-1467. Centers for Water and Wildland Resources, University of California, Davis (series: Wildland Resources Center report. Willard, D. 2000. A guide to the sequoia groves of California. Yosemite Association, Yosemite National Park. Citation Schmid, R. & Farjon, A. 2013. Sequoiadendron giganteum. The IUCN Red List of Threatened Species 2013: e.T34023A2840676. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en Disclaimer To make use of this information, please check the Terms of Use. External Resources For Images and External Links to Additional Information, please see the Red List website. © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 5 Appendix Habitats (http://www.iucnredlist.org/technical-documents/classification-schemes) Habitat Season Suitability Major Importance? 1. Forest -> 1.4. Forest - Temperate - Suitable Yes Use and Trade (http://www.iucnredlist.org/technical-documents/classification-schemes) End Use Local National International Construction or structural materials Yes No No Pets/display animals, horticulture No Yes Yes Establishing ex-situ production * No No No Threats (http://www.iucnredlist.org/technical-documents/classification-schemes) Threat Timing Scope Severity Impact Score 7. Natural system modifications -> 7.1. Fire & fire suppression -> 7.1.1. Increase in fire frequency/intensity Ongoing - - - Stresses: 1. Ecosystem stresses -> 1.2. Ecosystem degradation 2. Species Stresses -> 2.1. Species mortality 2. Species Stresses -> 2.2. Species disturbance 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.2. Competition Ongoing - Stresses: 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.1. Hybridisation 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.5. Inbreeding 8. Invasive & other problematic species & genes -> 8.3. Introduced genetic material - - Conservation Actions in Place (http://www.iucnredlist.org/technical-documents/classification-schemes) Conservation Actions in Place In-Place Research, Monitoring and Planning Action Recovery plan: Yes Systematic monitoring scheme: Yes © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 6 Conservation Actions in Place In-Place Land/Water Protection and Management Occur in at least one PA: Yes Percentage of population protected by PAs (0-100): 91-100 Area based regional management plan: Yes Invasive species control or prevention: Yes In-Place Species Management Harvest management plan: Yes Successfully reintroduced or introduced beningly: No Subject to ex-situ conservation: No In-Place Education Subject to recent education and awareness programmes: Yes Included in international legislation: No Subject to any international management/trade controls: No Conservation Actions Needed (http://www.iucnredlist.org/technical-documents/classification-schemes) Conservation Actions Needed 2. Land/water management -> 2.1. Site/area management Research Needed (http://www.iucnredlist.org/technical-documents/classification-schemes) Research Needed 3. Monitoring -> 3.4. Habitat trends Additional Data Fields Distribution Estimated area of occupancy (AOO) (km²): 142 Continuing decline in area of occupancy (AOO): Yes Estimated extent of occurrence (EOO) (km²): 13000 Number of Locations: 20 Lower elevation limit (m): 830 © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 7 Distribution Upper elevation limit (m): 2700 Population Continuing decline of mature individuals: Yes Population severely fragmented: Yes Habitats and Ecology Continuing decline in area, extent and/or quality of habitat: Yes Generation Length (years): 100 © The IUCN Red List of Threatened Species: Sequoiadendron giganteum – published in 2013. http://dx.doi.org/10.2305/IUCN.UK.2013-1.RLTS.T34023A2840676.en 8 The IUCN Red List Partnership The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. 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