|
Wildlife, Animals, and Plants
|
|
Introductory
SPECIES: Cupressus bakeri | Baker Cypress
ABBREVIATION :
CUPBAK
SYNONYMS :
NO-ENTRY
SCS PLANT CODE :
CUBA
COMMON NAMES :
Baker cypress
Modoc cypress
Siskiyou cypress
TAXONOMY :
The currently accepted scientific name of Baker cypress is Cupressus
bakeri Jeps. [10,19]. There are no recognized hybrids, varieties, or
forms. Two subspecies are recognized by some authors [10,19,25]:
Cupressus bakeri ssp. bakeri Jeps. Baker or Modoc cypress
Cupressus bakeri ssp. matthewsii Wolf Siskiyou cypress
Dodd [5,6] and Rafii [21,22] assert that population studies of
morphological and chemical diversity in Baker cypress do not support
subspecies status and believe that it should be discontinued. Hickman's
[10] taxonomic classification shall be used for this paper.
LIFE FORM :
Tree
FEDERAL LEGAL STATUS :
See OTHER STATUS
OTHER STATUS :
Siskiyou cypress (C. b. ssp. matthewsii) is endangered in Oregon [25].
COMPILED BY AND DATE :
Lora L. Esser, January 1994
LAST REVISED BY AND DATE :
NO-ENTRY
AUTHORSHIP AND CITATION :
Esser, Lora. 1994. Cupressus bakeri. In: Remainder of Citation
DISTRIBUTION AND OCCURRENCE
SPECIES: Cupressus bakeri | Baker Cypress
GENERAL DISTRIBUTION :
Baker cypress is restricted to northern California and southern Oregon.
Baker cypress (C. b. ssp. bakeri) occurs in Modoc, Plumas, Shasta, and
Siskiyou counties in California [18,25]. Siskiyou cypress (C. b. ssp.
matthewsii) has disjunct populations in the Siskiyou Mountains of
Josephine County, Oregon, and on Goosenest Mountain in Siskiyou County,
California [18,29]. The Bureau of Land Management administers the Baker
Cypress Natural Area and Timbered Crater Baker Cypress Natural Area,
both in Siskiyou and Modoc counties, California [16].
ECOSYSTEMS :
FRES20 Douglas-fir
FRES21 Ponderosa pine
FRES23 Fir - spruce
FRES26 Lodgepole pine
FRES28 Western hardwoods
FRES34 Chaparral - mountain shrub
STATES :
CA OR
ADMINISTRATIVE UNITS :
NO-ENTRY
BLM PHYSIOGRAPHIC REGIONS :
1 Northern Pacific Border
4 Sierra Mountains
KUCHLER PLANT ASSOCIATIONS :
K005 Mixed conifer forest
K007 Red fir forest
K008 Lodgepole pine - subalpine forest
K010 Ponderosa shrub forest
K012 Douglas-fir forest
K026 Oregon oakwoods
K030 California oakwoods
K033 Chaparral
K034 Montane chaparral
SAF COVER TYPES :
207 Red fir
211 White fir
218 Lodgepole pine
233 Oregon white oak
234 Douglas-fir - tanoak - Pacific madrone
243 Sierra Nevada mixed conifer
244 Pacific ponderosa pine - Douglas-fir
246 California black oak
247 Jeffrey pine
248 Knobcone pine
SRM (RANGELAND) COVER TYPES :
NO-ENTRY
HABITAT TYPES AND PLANT COMMUNITIES :
Baker cypress is a component of the northern interior cypress forest.
This habitat type is an open, fire-maintained, scrubby forest similar to
the knobcone pine (Pinus attenuata) forest. It is associated with
serpentine chaparral, and intergrades on less severe sites with upper
Sonoran mixed chaparral, montane chaparral, or knobcone pine forest
community types. On more mesic sites, the northern interior cypress
forest intergrades with mixed evergreen forest or montane coniferous
forest [11]. Baker cypress rarely forms pure stands [31]. The Timbered
Crater grove is associated with yellow pine (Pinus ponderosa and P.
jeffreyi) forest and suggests a transition zone between several plant
communities, including northern juniper woodland, yellow pine forest,
and sagebrush scrub. High elevation groves of Baker cypress in Plumas
County, California, are associated with red fir (Abies magnifica)
forest [29].
Species not already mentioned that are commonly associated with Baker
cypress include sugar pine (Pinus lambertiana), Brewer oak (Q. garryana
ssp. breweri), Sadler oak (Q. sadleriana), incense-cedar (Calocedrus
decurrens), Brewer spruce (Picea breweriana), Pacific yew (Taxus
brevifolia), juneberry (Amelanchier pallida), greenleaf manzanita
(Arctostaphylos patula), big sagebrush (Artemisia tridentata),
whitethorn ceanothus (Ceanothus cordulatus), wedgeleaf ceanothus (C.
cuneatus), deerbrush (C. integerrimus), Lemmon ceanothus (C. lemmonii),
squawcarpet (C. prostratus), snowbrush ceanothus (C. velutinus),
California redbud (Cercis occidentalis), birchleaf mountain-mahogany
(Cercocarpus betuloides), desertsweet (Chamaebatiaria millefolium), bush
chinquapin (Chrysolepsis sempervirens), low rabbitbrush (Chrysothamnus
viscidiflorus), Fremont silktassel (Garrya fremontii), western juniper
(Juniperus occidentalis), bitter cherry (Prunus emarginata), Klamath
plum (P. subcordata), western chokecherry (P. virginiana var. demissa),
skunkbush sumac (Rhus trilobata), baldhip rose (Rosa gymnocarpa)
creeping sage (Salvia sonomensis), antelope bitterbrush (Purshia
tridentata), gooseberry (Ribes spp.), buckwheat (Eriogonum spp.),
honeysuckle (Lonicera spp.), pussy paws (Calyptridium umbellatum),
larkspur (Delphinium spp.), bedstraw (Galium spp.), and goosefoot violet
(Viola purpurea) [2,5,11,27,29].
VALUE AND USE
SPECIES: Cupressus bakeri | Baker Cypress
WOOD PRODUCTS VALUE :
NO-ENTRY
IMPORTANCE TO LIVESTOCK AND WILDLIFE :
Rodents consume cypress seeds [1,18]. Cypresses are considered
undesirable forage for livestock, although young plants are browsed
[27].
PALATABILITY :
NO-ENTRY
NUTRITIONAL VALUE :
NO-ENTRY
COVER VALUE :
NO-ENTRY
VALUE FOR REHABILITATION OF DISTURBED SITES :
NO-ENTRY
OTHER USES AND VALUES :
NO-ENTRY
MANAGEMENT CONSIDERATIONS :
Baker cypress trees could be planted in the hot interior sections of
California as specimen trees, but are not feasible for windbreaks or
erosion control because of slow growth [31].
Seedlings of Baker cypress are susceptible to damping-off fungi [29].
Baker cypress (C. b. ssp. bakeri) is occasionally attacked by juniper
mistletoe (Phoradendron juniperinum ssp. juniperinum) in Plumas County,
and Siskiyou cypress (C. b. ssp. matthewsii) has been infected by
coryneum canker (Coryneum cardinale), which can kill trees [9].
BOTANICAL AND ECOLOGICAL CHARACTERISTICS
SPECIES: Cupressus bakeri | Baker Cypress
GENERAL BOTANICAL CHARACTERISTICS :
Baker cypress is a native, evergreen tree with a single stem and narrow
crown [12]. It grows from 33 to 99 feet (10-30 m) tall [10,31].
Juvenile leaves are from 0.08 to 0.4 inches (2-10 mm) long and may be
produced on seedlings for several years. They gradually give way to
mature leaves, which are 0.08 inches (2 mm) long. Ovulate cones occur
in clusters of 15 to 30 and are 0.8 to 1.6 inches (20-40 mm) in diameter
[1]. Staminate cones are 0.08 to 0.12 inches (3-4 mm) long [10]. The
bark of Baker cypress is partially exfoliating on the main trunk
[10,31]. A well-defined taproot and numerous lateral roots are formed
the first year [12].
RAUNKIAER LIFE FORM :
Phanerophyte
REGENERATION PROCESSES :
Baker cypress reproduces exclusively from seed. Cone production is
abundant. Staminate cones are produced on trees that are 6 to 7 years
old [31]. Ovulate cones are produced on trees that are 14 years of age
or older and require 2 years to mature [1]. They contain from 50 to 100
seeds per cone [1,31]. The cones are closed; they persist on the tree
until opened by the heat of a fire or desiccation due to age [12,29].
Seeds are shed gradually over several months after the cones are opened
by heat [29]. Detached cones will open, but they rarely result in
seedling establishment, usually due to the lack of a suitable seedbed
[1]. Seed dispersal is primarily by wind and rain [29].
Baker cypress requires bare mineral soil for germination and seedling
establishment. Seedlings of Baker cypress have been found in areas that
do not show signs of recent fire, but the seedlings area usually in the
immediate vicinity of fallen cypress trees and along skid roads [27].
Seedling mortality is greater in shaded situations with abundant litter
because of damping-off [1,29]. Seedlings are sensitive to excessive
moisture [31].
SITE CHARACTERISTICS :
Baker cypress is restricted to well-drained soils [1]. It occurs as
disjunct stands and isolated groves in the Sierra Nevada, the Cascade
Ranges, and the Siskiyou Mountains [21,29]. In the Siskiyou Mountains
Baker cypress occurs on serpentine soils; in the Sierra Nevada and
Cascade Range it occurs on basic volcanic rock. Soil profiles are
almost absent. On gentle slopes trees can be found on deeper soil
profiles; where Baker cypress is associated with red fir, a good humic
layer of dark brown soil exists [5].
Baker cypress is generally found at elevations from 3,795 to 7,042 feet
(1,150-2,134 m) on north- to northeast-facing slopes [5,29].
SUCCESSIONAL STATUS :
Facultative Seral Species
Cypress seedlings are shade intolerant and survive best in full sunlight
on bare mineral soil [29]. In the Mud Lake-Wheeler Peak area of Plumas
County, Baker cypress is being replaced by red and white (Abies
concolor) firs. Hundreds of saplings and pole-sized trees have died
with no indication of insects or disease. Competition of crowns for
light, shading of the ground, and accumulation of thick, black duff
characteristic of dense true fir stands have created an unfavorable
environment for the establishment and survival of Baker cypress [30].
According to Armstrong [1], cypresses of southern California are very
sensitive to lack of light, losing their foliage when growing in shade.
SEASONAL DEVELOPMENT :
Cypress (Cupressus spp.) shed pollen in late fall, winter, and spring.
Seeds mature 15 to 18 months after pollination. Ovulate cones ripen the
second season after pollination, but remain closed until opened by heat
or age [12,31].
FIRE ECOLOGY
SPECIES: Cupressus bakeri | Baker Cypress
FIRE ECOLOGY OR ADAPTATIONS :
Baker cypress is a fire-adapted, fire-dependent species. Reproduction
is usually restricted to burned sites [27]. The serotinous cones of
Baker cypress persist on the trees for years. Cone-opening is erratic,
slow, and almost negligible except when cones are exposed to extreme
heat; then it is rapid and uniform [32]. When opened by the heat of a
fire, the seeds fall on exposed mineral soil, and produce thickets of
seedlings [16,31]. Most seed falls in the first few months following
fire [32]. Fires that occur in late summer and fall, followed by winter
rains, ensure seed dissemination on bare mineral substrates [27,29]. No
information was available on fire-free intervals for communities
dominated by Baker cypress. However, Tecate cypress (Cupressus
guadalupenis var. forbesii), has an average interval between fires of 25
years, ranging from 15 to 63 years [1].
POSTFIRE REGENERATION STRATEGY :
Tree without adventitious-bud root crown
Crown residual colonizer (on-site, initial community)
Initial-offsite colonizer (off-site, initial community)
FIRE EFFECTS
SPECIES: Cupressus bakeri | Baker Cypress
IMMEDIATE FIRE EFFECT ON PLANT :
Baker cypress has thin, exfoliating bark which offers little fire
protection [29]. Most fires probably kill Baker cypress. Cones of the
California cypress open as the resin melts and boils. Rapid charring
of the thick cone scales extinguishes the flames, leaving seeds unburned
[1].
At the Rancho Santa Ana Botanic Garden in southern California on October
8, 1943, a severe fire killed all Siskiyou cypress (C. b. ssp.
matthewsii) trees. Some Baker cypress (C. b. ssp. bakeri) were killed
from the heat even though they were not burned [31].
DISCUSSION AND QUALIFICATION OF FIRE EFFECT :
NO-ENTRY
PLANT RESPONSE TO FIRE :
NO-ENTRY
DISCUSSION AND QUALIFICATION OF PLANT RESPONSE :
NO-ENTRY
FIRE MANAGEMENT CONSIDERATIONS :
Fires occurring too frequently in cypress groves may destroy them, as
reproduction could be eliminated before it had a chance to produce
cones. Conversely, fire suppression could threaten the species.
REFERENCES
SPECIES: Cupressus bakeri | Baker Cypress
REFERENCES :
1. Armstrong, Wayne P. 1966. Ecological and taxonomic relationships of
Cupressus in southern California. Los Angles, CA: California State
College. 129 p. Thesis. [21332]
2. Atzet, Thomas; Wheeler, David L. 1982. Historical and ecological
perspectives on fire activity in the Klamath Geological Province of the
Rogue River and Siskiyou National Forests. Portland, OR: U.S. Department
of Agriculture, Forest Service, Pacific Northwest Region. 16 p. [6252]
3. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals,
reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's
associations for the eleven western states. Tech. Note 301. Denver, CO:
U.S. Department of the Interior, Bureau of Land Management. 169 p.
[434]
4. Crosby, Bill. 1992. Our wildfire. Sunset. June: 62-72. [21662]
5. Dodd, Richard S.; Afzai-Rafii, Zara; Power, Ariel B. 1990. Biodiversity
within natural populations of Cupressus bakeri (Goosenest Mountain,
California). Ecologia Mediterranea. 16: 51-57. [21914]
6. Dodd, Richard S. 1992. Noteworthy collections: California. Madrono.
39(1): 79. [17536]
7. Eyre, F. H., ed. 1980. Forest cover types of the United States and
Canada. Washington, DC: Society of American Foresters. 148 p. [905]
8. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others].
1977. Vegetation and environmental features of forest and range
ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of
Agriculture, Forest Service. 68 p. [998]
9. Hawksworth, Frank G.; Wiens, Delbert. 1966. Observations on
witches'-broom formation, autoparasitism, and new hosts in Phoradendron.
Madrono. 18: 218-244. [18653]
10. Hickman, James C., ed. 1993. The Jepson manual: Higher plants of
California. Berkeley, CA: University of California Press. 1400 p.
[21992]
11. Holland, Robert F. 1986. Preliminary descriptions of the terrestrial
natural communities of California. Sacramento, CA: California Department
of Fish and Game. 156 p. [12756]
12. Johnson, LeRoy C. 1974. Cupressus L. cypress. In: Schopmeyer, C. S.,
technical coordinator. Seeds of woody plants in the United States.
Agric. Handb. 450. Washington, DC: U.S. Department of Agriculture,
Forest Service: 363-369. [7599]
13. Kruckeberg, Arthur R. 1984. California serpentines: flora, vegetation,
geology, soils and management problems. Publications in Botany Volume
48. Berkeley, CA: University of California Press. 180 p. [12482]
14. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation
of the conterminous United States. Special Publication No. 36. New York:
American Geographical Society. 77 p. [1384]
15. Ledig, F. Thomas. 1987. Genetic structure and the conservation of
California's endemic and near-endemic conifers. In: Elias, T. S., ed.
Conference on the conservation and management of rare and endangered
plants: Proceedings of symposium; [Date of conference unknown];
[Location of conference unknown]. Sacramento, CA: California Native
Plant Society: 587-594. [22218]
16. Little, Elbert L., Jr. 1975. Rare and local conifers in the United
States. Conservation Research Rep. No. 19. Washington, DC: U.S.
Department of Agriculture, Forest Service. 25 p. [15691]
17. Little, Elbert L., Jr. 1979. Checklist of United States trees (native
and naturalized). Agric. Handb. 541. Washington, DC: U.S. Department of
Agriculture, Forest Service. 375 p. [2952]
18. McMillan, Calvin. 1956. The edaphic restriction of Cupressus and Pinus
in the Coast Ranges of central California. Ecological Monographs. 26:
177-212. [11884]
19. Mitchell, Alan F. 1972. Conifers in the British Isles: A descriptive
handbook. Forestry Commission Booklet No. 33. London: Her Majesty's
Stationery Office. 322 p. [20571]
20. Posey, Clayton E.; Goggans, James F. 1967. Observations on species of
cypress indigenous to the United States. Circular 153. Auburn, AL:
Auburn University, Agricultural Experiment Station. 19 p. [20384]
21. Rafii, Zara; Cool, Laurence G.; Jonas, Robert; Zavarini, Eugene. 1992.
Chemical diversity in Cupressus bakeri. 1. Megagametophyte fatty acids.
Biochemical Systematics and Ecology. 20(1): 25-30. [20638]
22. Rafii, Zara; Cool, Laurence G.; Zavarin, Eugene. 1992. Variability of
foliar mono- and sesquiterpenoids of Cupressus bakeri. Biochemical
Systematics and Ecology. 20(2): 123-131. [20637]
23. Raunkiaer, C. 1934. The life forms of plants and statistical plant
geography. Oxford: Clarendon Press. 632 p. [2843]
24. Silen, Roy R.; Olson, Donald L. 1992. A pioneer exotic tree search for
the Douglas-fir region. Gen. Tech. Rep. PNW-GTR-298. Portland, OR: U.S.
Department of Agriculture, Forest Service, Pacific Northwest Research
Station. 44 p. [21668]
25. Smith, James Payne, Jr.; Berg, Ken. 1988. Inventory of rare and
endangered vascular plants of California. 4th ed. Special Publication
No. 1. Sacramento, CA: California Native Plant Society. 168 p. [7494]
26. Stickney, Peter F. 1989. Seral origin of species originating in northern
Rocky Mountain forests. Unpublished draft on file at: U.S. Department of
Agriculture, Forest Service, Intermountain Research Station, Fire
Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090]
27. Stone, Chester O. 1965. Modoc cypress, Cupressus bakeri Jeps., does
occur in Modoc County. Aliso. 6(1): 77-87. [25564]
28. U.S. Department of Agriculture, Soil Conservation Service. 1982.
National list of scientific plant names. Vol. 1. List of plant names.
SCS-TP-159. Washington, DC. 416 p. [11573]
29. Vogl, Richard J.; Armstrong, Wayne P.; White, Keith L.; Cole, Kenneth L.
1977. The closed-cone pines and cypress. In: Barbour, Michael G.; Major,
Jack, eds. Terrestrial vegetation of California. New York: John Wiley
and Sons: 295-358. [7219]
30. Wagener, Willis W.; Quick, C. R. 1963. Cupressus bakeri--an extension of
the known botanical range. Aliso. 5(3): 351-352. [25565]
31. Wolf, Carl B.; Wagener, Willis W. 1948. The New World cypresses. El
Aliso Series: Vol. 1. Anaheim, CA: Rancho Santa Ana Botanic Garden. 444
p. [20740]
32. Zedler, Paul H. 1986. Closed-cone conifers of the chaparral. Fremontia.
14(3): 14-17. [18648]
33. Wolf, C. B. 1948. Taxonomic and distributional status of the New World
cypresses. El Aliso. 1: 1-250. [20389]
Index
Related categories for Species: Cupressus bakeri
| Baker Cypress
|
 |