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Growth and Colonization of Western Redcedar by Vesicular-Arbuscular Mycorrhizae in Fumigated and Nonfumigated Nursery Beds
Tree Planter's Notes, Volume 42, No. 4 (1991) Growth and Colonization of Western Redcedar by Vesicular-Arbuscular Mycorrhizae in Fumigated and Nonfumigated Nursery Beds S. M. Berch, E. Deom, and T. Willingdon Assistant professor and research assistant, Department of Soil Science, University of British Columbia, Vancouver, BC, and manager, Surrey Nursery, British Columbia Ministry of Forests, Surrey, BC Western redcedar (Thuja plicata Donn ex D. Don) VAM. Positive growth responses of up to 20 times the seedlings were grown in a bareroot nursery bed that had nonmycorrhizal controls occurred under conditions of limited been fumigated with methyl bromide. Seedlings grown in soil phosphorus. Incense-cedar, redwood, and giant sequoia fumigated beds were stunted and had purple foliage. seedlings in northern California nursery beds are routinely Microscopic examination showed that roots from these inoculated with Glomus sp. (Adams et al. 1990), as seedlings were poorly colonized by mycorrhizae, and only by experience has shown that the absence of VAM after soil fine vesicular-arbuscular mycorrhizae. In contrast, roots from fumigation leads to phosphorus deficiency and poor growth. seedlings grown in non-fumigated beds had larger shoots and When western redcedars in fumigated transplant beds at green foliage and were highly colonized by both fine and the British Columbia Ministry of Forest's Surrey Nursery coarse vesicular-arbuscular mycorrhizae. Tree Planters' began to show signs of phosphorus deficiency, a deficiency Notes 42(4):14-16; 1991. of mycorrhizal colonization was suspected. Many studies have demonstrated improved P status of VAM-inoculated Species of cypress (Cupressaceae) and yew plants (see Harley and Smith 1983). -
Giant Sequoia Insect, Disease, and Ecosystem Interactions1
Giant Sequoia Insect, Disease, and Ecosystem Interactions1 Douglas D. Piirto2 Abstract: Individual trees of giant sequoia (Sequoia gigantea [Lindl.] afflict and kill other trees." Similarly Hartesveldt (1962) Decne.) have demonstrated a capacity to attain both a long life and very concurred that "Sequoia's longevity and great size have large size. It is not uncommon to find old-growth giant sequoia trees in their native range that are 1,500 years old and over 15 feet in diameter at been attributed by nearly all writers, popular and scientific, breast height. The ability of individual giant sequoia trees to survive over to its few insect and fungus parasites and the remarkable such long periods of time has often been attributed to the species high resistance of the older trees to damage or death by fire. resistance to disease, insect, and fire damage. Such a statement, however, is There is no record of an individual sequoia living in its a gross oversimplification, given broader ecosystem and temporal interac- tions. For example, why isn't there a greater representation of young-growth natural range as having been killed by either fungus or insect giant sequoia trees throughout the mixed-conifer belt of the Sierra Nevadas? attack." Even as recently as 1991 Harlow and others (1991) What other factors, in addition to physical site characteristics, limit giant stated: "Insects and fungi cause but minor damage, and no sequoia to its present range and grove boundaries? How does fire and fire large Bigtree killed by them has ever been found." frequency affect disease and insect interrelationships in the giant sequoia/ mixed-conifer ecosystem? Are current forest management strategies (e.g., It is finally being recognized that giant sequoia is fire suppression, prescribed burning programs) affecting these interactions? subject to the same natural forces as other tree species (Bega Giant sequoia trees are subject to the same natural forces (e.g., insect and 1964, Harvey and others 1980, Parmeter 1987, Piirto 1977, disease organisms) as other tree species. -
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Annals of Plant Sciences 7.4 (2018) pp. 2179-2186 Research Article Seed and seedling morphology of two near threatened Indian species: Cryptomeria japonica and Cupressus cashmeriana (Cupressaceae sensu lato) Sonali Ray1* and Nanda Dulal Paria2 1Department of Botany, Surendranath College, 24/2, Mahatma Gandhi Road, Kolkata- 700009., West Bengal, India 2Professor in Botany (retired), Department of Botany, University of Calcutta, 35 Ballygunge Circular Road, Kolkata- 700019, West Bengal, India. Received: 2/23/2018; Revised: 2/28/2018; Accepted: 3/17/2018 Abstract: Seed and Seedling morphology of two species of Cupressaceae – Cupressus cashmeriana Royle ex Carriéreand Cryptomeria japonica (Thunb. Ex L.f.) D. Don have been studied using light microscope (LM) and scanning electron microscope (SEM). Both the species are categorized as Near Threatened (NT) in IUCN Red List Category (2013). For characterization of seed, different parameters like shape, size, base, apex, surface were considered. For the study of seedlings, the parameters like germination pattern, root, hypocotyl, number of paracotyledons, number and nature of first leaf and subsequent leaves have been characterized. The seed and seedling characters as studied in this investigation are important as taxonomic markers for identification purpose. Keywords: Seedling morphology, identification, Cupressus cashmeriana Royle ex Carriére and Cryptomeria japonica (Thunb. Ex L.f.) D. Don. Introduction Cupressus cashmeriana Royle ex Carriére and phylogenetic studies (Damon et al, 2006), molecular Cryptomeria japonica (Thunb. Ex L.f.) D. Don belong studies (Rushforth, 2003), anatomy (Romàn-Jordàn to family Cupressaceae sensu lato. Cupressus et al., 2016) and palynology (Danti et al., 2010) for cashmeriana Royle ex Carriére is an evergreen tree, Cupressus cashmeriana. -
Why Are Coast Redwood and Giant Sequoia Not Where They Are Not?1
Proceedings of the Coast Redwood Science Symposium—2016 Why Are Coast Redwood And Giant Sequoia Not Where They Are Not?1 2 W.J. Libby Abstract Models predicting future climates and other kinds of information are being developed to anticipate where these two species may fail, where they may continue to thrive, and where they may colonize, given changes in climate and other elements of the environment. Important elements of such predictions, among others, are: photoperiod; site qualities; changes in levels and yearly patterns of temperature, wind, fog and precipitation; the effects of these on interactions with other biota at each site; the effects of changes in fire frequency and intensity; the availability of seeds and seed vectors; and the effects of human activity. Examples are presented, with focus on fire and human activity. Natural migration may need assistance. Establishing groves far from the native ranges is advocated. Keywords: assisted colonization, assisted migration, climate change, fire, Sequoia, Sequoiadendron When preparing this talk and then paper, it became increasingly clear that it is more of an Op-Ed than a comprehensive review, and is meant for people interested in and familiar with coast redwood (Sequoia sempervirens (D. Don) Endl.) and giant sequoia (Sequoiadendron giganteum (Lindl.) Buchholz). Thus, four background references are provided, and they in turn provide detail on many of the topics covered. The final two references provide background on future speculative scenarios. Possible responses to such future scenarios are suggested. Coast redwood’s current natural latitudinal range begins with discontinuous canyon-bottom populations near the southern Monterey County border, extends north through increasingly- continuous coastal and generally-separated interior populations, and stops just north of the Oregon/California border. -
Giant Sequoia Management in National Parks 1
in: Aune, rnuip s., teen, coora. iyy*. rroceeainss oi me symposium on uian. sc^uiaa. '«'" ^.o^c ... the ecotystea and society; 1992 June 23-25; Visalia, CA. Albany, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Research Station: 109-115. Objects or Ecosystems? PUB #267 Giant Sequoia Management in National Parks 1 David J. Parsons2 Abstract: Policies and programs aimed at protecting giant sequoia the effects of such external threats as air pollution and (Sequoiadendron giganteum) in the national parks of the Sierra Nevada projected human induced climadc change. The challenges have evolved from the protection of individual trees to the preservation of entire ecosystems. We now recognize that the long-term preservation of associated with assuring the long-term preservation of giant giant sequoia depends on our ability to minimize and mitigate the influences sequoia have become increasingly complicated as we have of human activities. National Park Service management strategies for giant learned more about the complexity and inter-relatedness of sequoia focus on the restoration of native ecosytem processes. This includes the greater Sierra Nevada ecosystem. the use of prescribed fire to simulate natural ignitions as well as the movement of visitor facilities out of the groves. Basic research is being This paper briefly reviews the history of giant sequoia carried out to improve our understanding of the factors infuencing giant management in the National Parks of the Sierra Nevada, sequoia reproduction, growth, and survival. Future management decisions emphasizing a gradually improved understanding of giant must recognize that giant sequoia are only part of a complex ecosystem; they sequoia ecosystems and how management has attempted to cannot be managed as objects in isolation of their surroundings. -
The Taxonomic Position and the Scientific Name of the Big Tree Known As Sequoia Gigantea
The Taxonomic Position and the Scientific Name of the Big Tree known as Sequoia gigantea HAROLD ST. JOHN and ROBERT W. KRAUSS l FOR NEARLY A CENTURY it has been cus ing psychological document, but its major,ity tomary to classify the big tree as Sequoia gigan vote does not settle either the taxonomy or tea Dcne., placing it in the same genus with the nomenclature of the big tree. No more the only other living species, Sequoia semper does the fact that "the National Park Service, virens (Lamb.) End!., the redwood. Both the which has almost exclusive custodY of this taxonomic placement and the nomenclature tree, has formally adopted the name Sequoia are now at issue. Buchholz (1939: 536) pro gigantea for it" (Dayton, 1943: 210) settle posed that the big tree be considered a dis the question. tinct genus, and he renamed the tree Sequoia The first issue is the generic status of the dendron giganteum (Lind!.) Buchholz. This trees. Though the two species \differ con dassification was not kindly received. Later, spicuously in foliage and in cone structure, to obtain the consensus of the Calif.ornian these differences have long been generally botanists, Dayton (1943: 209-219) sent them considered ofspecific and notofgeneric value. a questionnaire, then reported on and sum Sequoiadendron, when described by Buchholz, marized their replies. Of the 29 answering, was carefully documented, and his tabular 24 preferred the name Sequoia gigantea. Many comparison contains an impressive total of of the passages quoted show that these were combined generic and specific characters for preferences based on old custom or sentiment, his monotypic genus. -
Street Tree Inventory Report Hillsdale Neighborhood August 2016 Street Tree Inventory Report: Hillsdale Neighborhood August 2016
Street Tree Inventory Report Hillsdale Neighborhood August 2016 Street Tree Inventory Report: Hillsdale Neighborhood August 2016 Written by: Kat Davidson, Angie DiSalvo, Julie Fukuda, Jim Gersbach, Jeremy Grotbo, and Jeff Ramsey Portland Parks & Recreation Urban Forestry 503-823-4484 [email protected] http://portlandoregon.gov/parks/treeinventory Hillsdale Tree Inventory Organizers: Jim Keiter Staff Neighborhood Coordinator: Jim Gersbach Data Collection Volunteers: Dennis Alexander, Richard Anderson, William Better, Ben Brady, Brian Brady, Julia Brown, Marty Crouch, Hannah Davidson, April Ann Fong, Lise Gervais, Margaret Gossage, Karen Henell, Jim Keiter, John Mills, Pat Ruffio, Jerry Sellers, Kristin Sellers, Mimi Siekmann, Haley Smith, Nancy Swaim, Mark Turner, Loris Van Pelt, Paige Witte, and Maggie Woodward Data Entry Volunteers: Michael Brehm, Nathan Riggsby, and Eric Watson Arborist-on-Call Volunteers: Will Koomjian GIS Technical Support: Josh Darling, Portland Parks & Recreation Financial Support: Portland Parks & Recreation Cover Photos (from top left to bottom right): 1) Colorful foliage on a golden Deodar cedar (Cedrus deodara 'Aurea'). 2) The deep green leaves of a quaking aspen (Populus tremuloides). 3) Unusual peeling bark on a young madrone (Arbutus menziesii). 4) A vivid fuchsia bloom on a magnolia (Magnolia sp.) 5) The developing cone of a rare China-fir Cunninghamia( lanceolata). 6) Unusually shaped leaves on a tulip poplar (Liriodendron tulipifera). 7) The pendant foliage of a weeping giant sequoia (Sequoiadendron giganteum 'Pendulum'). 8) Multicolored scaly foliage on a variegated elkhorn cedar (Thujopsis dolobrata 'Variegata'). ver. 10/17/2016 Portland Parks & Recreation 1120 SW Fifth Avenue, Suite 1302 Portland, Oregon 97204 (503) 823-PLAY Commissioner Amanda Fritz www.PortlandParks.org Director Mike Abbaté Contents Key Findings ......................................... -
Discover Giant Sequoia National Monument
United States Department of Agriculture Discover the Giant Sequoia National Monument Western Divide Ranger District Hume Lake Ranger District The Monument is named for the native Giant Sequoia tree, Sequoiadendron giganteum, the world’s largest tree. Sequoias can tower more than 300 feet high and reach diameters of 40 feet. Out of approximately 67 groves in the Sierra, the Monument contains 38. On April 15, 2000, President William J. Clinton, by proclamation, In addition, almost all National Forest System land created the Giant Sequoia National Monument. The Giant Sequoia is available for you to choose your own camping National Monument is located within Sequoia National Forest in the spot and this is called dispersed camping. Southern Sierra Nevada Mountains of California. Gateways are Highway Remember to obtain a campfire permit if you plan 180 east of Fresno, Highway 190 east of Porterville, County Road M-56 to make your own camp and pack out all your trash. east of California Hot Springs, and Highway 178 east and north of Bakersfield. The Monument encompasses approximately 327,769 acres Several refurbished historic cabins can be rented for over-night of federal land managed by the Sequoia National Forest, Western Divide visits: Big Meadows Guard Station near Hume Lake, Poso Station and Hume Lake Ranger Districts. near Sugarloaf and Glenville, Frog Meadow Guard Station near Tobias Peak, and Mountain Home Guard Station near Balch Park The landscape is as spectacular as its 38 groves of giant sequoia. Elevation and Mountain Home Demonstration State Forest. Please contact the climbs from around 1,000 to 9,700 feet over a distance of only a few Districts for more miles, capturing an extraordinary array of habitats within a relatively information . -
Density Effects on Giant Sequoia (Sequoiadendron Giganteum) Growth Through 22 Years: Implications for Restoration and Plantation Management
Density Effects on Giant Sequoia (Sequoiadendron giganteum) Growth Through 22 Years: Implications for Restoration and Plantation Management Robert A. York, Kevin L. O’Hara, and John J. Battles Giant sequoia were planted at various densities and tracked for 22 years to quantify the effect of growing space on diameter, height, stem volume, branch diameter, and branch density. Beginning after just 4 years and continuing through year 22, both stem diameter and height growth were highly sensitive to initial planting density (expressed in this case as horizontal growing space per tree) within the tested range of 3.7 to 28.4 m2. Through 22 years, treatments allocating the greatest growing space per tree had greater volume per tree with no tradeoff yet observed in stand level volume growth. Branch diameter along the stem generally increased with growing space, but branch density did not change. To meet objectives, this study demonstrates that management strategies should be tailored to species’ specific growth strategies. Giant sequoia is characterized by rapid early growth coupled with exceptionally low mortality, which has relevance in both native grove restoration as well as plantation management contexts. The measurements in this study suggest either planting at low density ABSTRACT or thinning giant sequoia very early in dense stands if the objective is to increase individual tree growth rates without a corresponding reduction in stand volume. Young stands developing following high-severity fires may benefit from low-severity prescribed burns if objectives are to increase average stem growth or the rate of canopy recruitment. Keywords: spacing study, density management, intraspecific competition nderstanding the nature of competition between plants for In native groves, management objectives revolve around cohort es- finite resources is fundamental to the study of vegetation tablishment and canopy recruitment following regeneration failures Udynamics (Hutchings and Budd 1981). -
26 Extreme Trees Pub 2020
Publication WSFNR-20-22C April 2020 Extreme Trees: Tallest, Biggest, Oldest Dr. Kim D. Coder, Professor of Tree Biology & Health Care / University Hill Fellow University of Georgia Warnell School of Forestry & Natural Resources Trees have a long relationship with people. They are both utility and amenity. Trees can evoke awe, mysticism, and reverence. Trees represent great public and private values. Trees most noticed and celebrated by people and communities are the one-tenth of one-percent of trees which approach the limits of their maximum size, reach, extent, and age. These singular, historic, culturally significant, and massive extreme trees become symbols and icons of life on Earth, and our role model in environmental stewardship and sustainability. What Is A Tree? Figure 1 is a conglomeration of definitions and concepts about trees from legal and word definitions in North America. For example, 20 percent of all definitions specifically state a tree is a plant. Concentrated in 63% of all descriptors for trees are four terms: plant, woody, single stem, and tall. If broad stem diameter, branching, and perennial growth habit concepts are added, 87% of all the descriptors are represented. At its most basic level, defining a tree is not species based, but is a structural definition. A tree is represented by a type of plant architecture recognizable by non-technical people. The most basic concepts for defining a tree are — a large, tall, woody, perennial plant with a single, unbranched, erect, self-supporting stem holding an elevated and distinct crown of branches, and which is greater than 10 feet in height and greater than 3 inches in diameter. -
Two Distinct Himalayan Cypress Species Cupressus Tortulosa and Cupressus Cashmeriana with Additional Comparison to Cupressus Torulosa
Bull. CCP 3 (3): 99-115. (12.2014) D. Mаеrki Two distinct Himalayan cypress species Cupressus tortulosa and Cupressus cashmeriana with additional comparison to Cupressus torulosa In a previous article (Mаеrki 2013b), the trees grown in France, Italy and Switzerland under the label Cupressus cashmeriana Carrière were investigated. It was discovered that the cypresses grown in France are different from those cultivated in Italy, which better match the material collected by Griffith in Bhutan and described by him under the name Cupressus tortulosa. A summary of the main differences has been proposed (Mаеrki, 2013b: 49-50) together with analysis of Carrière’s protologue (1867) and discussion of the correct origin of the French plants in “Tibet” (now Arunachal Pradesh in India). The scope of the present article is to detail these differences with new observations and statistical data. Cupressus torulosa D.Don, Cupressus tortulosa and Cupressus cashmeriana are all growing west to 1 east on the southern slopes of the Himalaya in well separated distribution ranges ; west Nepal, and Himachal Pradesh and Uttarakhand in India, for C. torulosa, Bhutan for C. tortulosa and Arunachal Pradesh (India) for C. cashmeriana. All populations of each species are scattered in different valleys. It is quite likely that the compartmentalisation of these populations over several millions years allowed speciation processes from a common ancestor. There are also lots of planted trees near temples, monasteries and fortresses whose origins are not recorded. Several wild stands are very difficult to access, sometimes almost impossible above high cliffs, and are still in need of investigation; further taxa could possibly yet be discovered. -
Naturalization of Sequoiadendron Giganteum (Cupressaceae) in Montane Southern California Rudolf Schmid University of California, Berkeley
Aliso: A Journal of Systematic and Evolutionary Botany Volume 30 | Issue 1 Article 4 2012 Naturalization of Sequoiadendron giganteum (Cupressaceae) in Montane Southern California Rudolf Schmid University of California, Berkeley Mena Schmid Follow this and additional works at: http://scholarship.claremont.edu/aliso Part of the Botany Commons, Ecology and Evolutionary Biology Commons, and the Forest Biology Commons Recommended Citation Schmid, Rudolf and Schmid, Mena (2012) "Naturalization of Sequoiadendron giganteum (Cupressaceae) in Montane Southern California," Aliso: A Journal of Systematic and Evolutionary Botany: Vol. 30: Iss. 1, Article 4. Available at: http://scholarship.claremont.edu/aliso/vol30/iss1/4 Aliso, 30(1), pp. 19–32 ’ 2012, Rancho Santa Ana Botanic Garden NATURALIZATION OF SEQUOIADENDRON GIGANTEUM (CUPRESSACEAE) IN MONTANE SOUTHERN CALIFORNIA RUDOLF SCHMID1,3 AND MENA SCHMID2 1Department of Integrative Biology, University of California, Berkeley, California 94720-3140, USA ([email protected]); 2Somerville, Massachusetts 02144, USA([email protected]) 3Corresponding author ABSTRACT After the August 1974 fire in the upper Hall Canyon area on the southwestern flank of Black Mountain in the northwestern San Jacinto Mountains, Riverside Co., California, the United States Forest Service revegetated the burn in the mixed-conifer forest with the Sierra Nevada endemic Sequoiadendron giganteum (Cupressaceae). On 1 May 2009 a GPS census starting at the head of Hall Canyon revealed both in the canyon and upslope beyond it at least 157 individuals in the vicinity of the Black Mountain Trail, plus an outlier 450 m distant near the summit. This species alien to southern California is regenerating prolifically on Black Mountain, as revealed by multiple age classes, from juveniles (seedlings and saplings) about 20– 60 cm tall to young adult trees over 6 m tall, up to about 40 years old, and reproductively mature.