SPECIES: Quercus gambelii
Simonin, Kevin A. 2000. Quercus gambelii. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/ .
Quercus gambelii Nutt. var. bonina S.L. Welsh, Goodhope oak
Quercus gambelii Nutt. var. gambelii, Gambel's oak
Hybridization between oak species is common. Gambel oak hybridizes readily with other oak species and has influenced the evolution of several oaks . Hybridization occurs with Arizona white oak (Q. arizonica) , bur oak (Q. macrocarpa) [30,201], chinkapin oak (Q. muehlenbergii), gray oak (Q. grisea) [2,84,201], Mohr's oak (Q. mohriana) , and shrub live oak (Q. turbinella) [43,201].
No special status
Gambel oak occurs from New Mexico west to Arizona and southwestern Nevada and north to Utah, Colorado and southeastern Wyoming . Isolated patches occur in Texas . The Natural Resource Conservation Service provides a map of Gambel oak's distribution in the United States (http://plants.usda.gov/plants/cgi_bin/topics.cgi).
FRES21 Ponderosa pine
FRES33 Southwestern shrubsteppe
FRES34 Chaparral-mountain shrub
FRES36 Mountain grasslands
FRES40 Desert grasslands
6 Upper Basin and Range
7 Lower Basin and Range
11 Southern Rocky Mountains
12 Colorado Plateau
K018 Pine-Douglas-fir forest
K019 Arizona pine forest
K020 Spruce-fir-Douglas-fir forest
K021 Southwestern spruce-fir forest
K023 Juniper-pinyon woodland
K031 Oak-juniper woodland
K032 Transition between K031 and K037
K037 Mountain-mahogany-oak scrub
K038 Great Basin sagebrush
K055 Sagebrush steppe
K057 Galleta-threeawn shrubsteppe
K058 Grama-tobosa shrubsteppe
220 Rocky Mountain juniper
237 Interior ponderosa pine
241 Western live oak
107 Western juniper/big sagebrush/bluebunch wheatgrass
109 Ponderosa pine shrubland
207 Scrub oak mixed chaparral
401 Basin big sagebrush
402 Mountain big sagebrush
403 Wyoming big sagebrush
404 Threetip sagebrush
405 Black sagebrush
408 Other sagebrush types
411 Aspen woodland
412 Juniper-pinyon woodland
413 Gambel oak
415 Curlleaf mountain-mahogany
416 True mountain-mahogany
417 Littleleaf mountain-mahogany
418 Bigtooth maple
503 Arizona chaparral
504 Juniper-pinyon pine woodland
505 Grama-tobosa shrub
509 Transition between oak-juniper woodland and mahogany-oak association
In the southern extent of its distribution, Gambel oak occupies a minor role as an associate within ponderosa pine (Pinus ponderosa) and mixed-conifer habitats. Moving north, long-lived Gambel oak clones form dominant to monotypic overstories .
Harper and others  constructed a list of common plant associates in a 1985 literature review. The following table lists common plant associates of Gambel oak.
|SHRUBS and TREES|
|Pinus ponderosa||ponderosa pine||B,C,D|
|Populus tremuloides||quaking aspen||A,B,C,E|
|Purshia tridentata||antelope bitterbrush||A,B,C,D|
|Rosa spp.||wild rose||A,B,D,E|
|Achillea millefolium||western yarrow||A,B,C,E|
|Koeleria macrantha||prairie junegrass||A,B,D|
Kunzler and others  evaluated 23 Gambel oak brush stands in central and northern Utah to compare presence or absence of major plant associates. Gambel oak stands on average supported 25 plant species; cheatgrass (Bromus tectorum) and stickywilly (Galium aparine) were the 2 most abundant species. The most abundant shrub associate was mountain snowberry (Symphoricarpos oreophilus).
Gambel oak is a typical riparian species in New Mexico, occurring from 6,580 to 8,080 feet (2,006 - 2,463 m) within the Black and Sacramento mountain ranges .
Gambel oak is a dominant species in the central Utah mountain brush zone at 6,500 to 7,800 feet (1,981-2,377 m) on southern exposures. On northern exposures Gambel oak either shares dominance with bigtooth maple (Acer grandidentatum) or is completely replaced by bigtooth maple . Bigtooth maple is a common Gambel oak associate at the southern end of the Wasatch Mountains. On the west flank of the southern and middle Wasatch range, Gambel oak and bigtooth maple form a dense woodland .
In Arizona Gambel oak is represented as shrub thickets over the majority of its range. It occurs as a tree throughout the ponderosa pine habitat type. The habit of Gambel oak within ponderosa pine-Gambel oak habitat types corresponds to the overall density of ponderosa pine. In dense ponderosa pine stands, Gambel oak is sparse and short; stems are taller and clumped in open stands . At an elevation range of 8,000 to 8,600 feet (2,440-2,620 m) in Arizona, Gambel oak is subdominant to ponderosa pine with southwestern white pine (Pinus strobiformis) . On heavier-textured soils in Colorado, serviceberry (Amelanchier spp.) is an important associate .
Published classifications listing Gambel oak as an indicator or dominant are
A classification of forest habitat types of the northern portion of the Cibola National Forest, New Mexico 
A classification of forest habitat types of the Lincoln National Forest, New Mexico 
Douglas-fir habitat types of northern Arizona 
Classification of the forest vegetation of Colorado by habitat type and community type 
Forest Vegetation on National Forests in the Rock Mountain and Intermountain Regions: habitat and community types 
Forest vegetation of the Medicine Bow National Forest in southwestern Wyoming: a habitat classification 
Classification of the forest vegetation on the National Forests of Arizona and New Mexico 
Climax forest series of northern New Mexico and southern Colorado 
Forest habitat types south of the Mogollon Rim, Arizona and New Mexico 
A classification of forest habitat types of northern new Mexico and southern Colorado 
Forest habitat types in the Apache, Gila and part of the Cibola National Forests, Arizona and New Mexico 
Grassland, shrubland and forestland habitat types of the White River-Arapaho National Forest 
Forest vegetation of the Routt National Forest in Northwestern Colorado: a habitat classification 
Forest vegetation of the Gunnison and parts of the Uncompahgre National Forests: a preliminary habitat type classification 
Forest and woodland habitat types (plant associations) of northern New Mexico and northern Arizona 
A classification of spruce-fir and mixed conifer habitat types of Arizona and New Mexico 
Aspen community types of Utah 
A classification of forest habitat types: southern Arizona and portions of the Colorado Plateau 
Plant associations (habitat types) of the forests and woodlands of Arizona and New Mexico 
A management-oriented classification of pinyon-juniper woodlands of the Great Basin 
Forest habitat types on the Medicine Bow National Forest, southeastern Wyoming: preliminary report 
Coniferous forest habitat types of central and southern Utah 
Gambel oak is a good source of fuel wood. Within the Intermountain Region, productivity is high enough to exceed economic thresholds, and profuse vegetative regeneration is ideal for a fuel wood management cycle .
Gambel oak is a good source of firewood that produces little smoke and soot. An average weight per standard cord, based upon 80 cubic feet of solid wood in pounds, is summarized below :
|Oven Dry||Air-dry (12% moisture)||Green (65% moisture)|
52 % more than quaking aspen (Populus tremuloides)
42 % more than ponderosa pine
36 % more than lodgepole pine (Pinus contorta)
24 % more than Rocky Mountain juniper (Juniperus scopulorum)
Gambel oak was compared with Colorado pinyon (Pinus edulis), alligator juniper (Juniperus deppeana), ponderosa pine and eastern redcedar (Juniperus virginiana) for specific wood product values. An average comparative index based upon a weighted combination of specific strength values is summarized below . Final index values were obtained at 20% moisture content.
|Property||Gambel oak||Colorado pinyon||alligator juniper||ponderosa pine||eastern redcedar|
Small-diameter stems of Gambel oak that are reasonably straight make ideal fenceposts that are decay-resistant and more durable than other oaks . Untreated posts outlast both Emory oak (Quercus emoryi) and Arizona white oak .
Gambel oak is an ecologically important species providing food and shelter for many wildlife species. Type and degree of wildlife use corresponds with Gambel oak habit. Brushy growth forms (thickets less than 25 ft2 (2.3 m2) and stems less than 15 feet (4.57 m) tall) are utilized as browse by big game and provide habitat for rabbits and rodents. Young pole stands provide sites for foliage-nesting birds. Mature growth forms provide maximum acorn yield for squirrels, birds, elk, and deer. Old stands containing large amounts of dead crown and hollow boles or limbs provide nesting sites for small mammals and birds .
Avian: Gambel oak acorns are an important mast crop in many areas. Acorns are a preferred food for band-tailed pigeons during fall and winter. Merriam turkeys also utilize acorns as a major part of their diet . Abert's squirrels feed upon Gambel oak acorns . When a good crop is available, acorns may provide up to 40% of Abert's squirrel fall diet . Patton and others  observed squirrels using hollow Gambel oaks over 10 inches (25.4 cm) d.b.h. as nesting sites. Abert's squirrels prefer ponderosa pine forests (201 to 250 trees per acre) where Gambel oak is within a 12 to 14 inch d.b.h. class occurring as 1or 2 trees per acre .
Gambel oak trees within the ponderosa pine-Gambel oak forests of Arizona provide perching and nest sites for the Mexican spotted owl [81,82]. Illegal cutting of large oak trees within these forests is considered a serious problem for Mexican spotted owl management . Gambel oak is used significantly more (p< 0.01) by juvenile Mexican spotted owls as roosts during dispersal in the fall (August-October) than in winter (November-April) . Conifer/oak forests with relatively high densities of Gambel oak along canyon bottoms of New Mexico are preferred roost sites for Mexican spotted owls .
Within a Gambel oak brush community in northern Utah, Marti  observed 6 permanent residents: California quail, ring-necked pheasants, scrub jays, black-billed magpies, black-capped chickadees, and rufous-sided towhees. Marti also provides a complete list of birds observed and found nesting.
Mountain shrub habitats where Gambel oak is codominant with serviceberry provide a summer habitat for Columbia sharp-tailed grouse of northwestern Colorado . In Utah, Gambel oak may provide nesting sites for sharp-shinned hawks . Pygmy owls inhabit ponderosa pine-Gambel oak forest types within the Dixie National Forest, Utah .
Big game: Gambel oak is a major forage species for deer and elk in Utah . Gambel oak is moderately used, relative to other forage and browse species, by Rocky Mountain mule deer in winter and spring with heavier use occurring in summer and fall . In its southern range, Gambel oak is a desirable species for desert mule deer and white-tailed deer in the San Cayetano and Dos Cabezas mountains of southeastern Arizona. Greatest use of Gambel oak occurs mid-July to October, with white-tailed deer showing greater utilization than mule deer. Gambel oak, however, is not located in habitats used by mule and white-tailed deer of Arizona during the winter .
Gambel oak communities in Colorado provide important winter ranges for big game animals . Based upon a review of 3 studies, Kufeld  reports Gambel oak as highly valuable winter forage for Rocky Mountain elk. Smith  and Smith and Hubbard  monitored winter forage preference of deer in Utah. Gambel oak ranked 7th out of 17 forage species based on time spent browsing and plant weight consumed. Mule deer and white-tailed deer utilized new growth and sprouts as forage [107,171]. Gambel oak ranges in southwestern Colorado provide the majority of black bear spring habitat  and fall food for black bear in southwestern Colorado .
In Colorado, bighorn sheep utilize Gambel oak as a minor component of their summer diet. On low elevation summer ranges, Gambel oak may comprise up to 17% of the June diet , although, in most cases, bighorn sheep avoid dense stands of Gambel oak . Within north-central Utah, porcupines use Gambel oak as their primary winter food and cover source .
Acorns can also provide a food source for collared peccary in Arizona .
Gambel oak may contribute up to 50% of diet without cattle showing any ill effects. Poisoning occurs when more than 50% is consumed, with death often resulting when more than 75% of cattle's diet is Gambel oak . Freezing enhances toxic properties of Gambel oak browse; young foliage turned black by freezing is extremely toxic .
The palatability of Gambel oak to livestock and wildlife species in several western states has been rated as follows  :
|Small nongame birds||Poor||Poor||Good|
|Upland game birds||Good||Good||Good|
Mature and juvenile Gambel oaks provide valuable forage with nitrogen and energy in excess of maintenance requirements for Spanish goats . At 5.4% crude protein, Gambel oak does not meet the protein requirement of wintering mule deer . Protein content of Gambel oak leaves was found to decrease starting June to September while phosphorus and gross energy remained constant . As winter browse, Gambel oak is low in essential nutrients , with crude protein less than 10% .
The percent nutrient content of Gambel oak during January from 9 geographic areas throughout Colorado is summarized below :
|Nutrient||Mean||Coefficient of variation (%)|
|Dry matter component||64.1||1.7|
|In-vitro digestible dry matter||28.1||3.7|
Welch  reports Gambel oak to have 26.6% in-vitro digestibility and a crude protein content of 5.3% in winter.
Dick and others  compared chemical composition of juvenile and mature Gambel oak:
|Juvenile oak||Mature oak|
|Dry matter (%)||35.2||44.8|
|Cell wall (%)||36.2||43.8|
|Gross energy (Kcal/g)||4.6||4.3|
|Tannin (mg protein ppt./mg sample)||0.231||0.176|
|Tannin (mg tannic acid equivalent/g)||40.4||34.7|
Juvenile Gambel oak contains higher tannin levels than mature trees, but also has higher digestibility of dry matter and fiber . Concentration of tannins in Gambel oak forage is greatest in spring .
A nutritional difference exists between Gambel oak sprouts on burned and unburned areas. Postfire bud tissue is higher in tannin content (4.1 mg/100 mg burned plant tissue compared to unburned with 3.4 mg/100 mg). Burned stem tannin content was twice that of unburned, 1.6 to 0.7 respectively. Although high in tannin, postburn buds had higher nutritional value than either buds and twigs of unburned areas or twigs on burned areas :
|Crude protein (%)||Phosphorus (%)||Digestibility (%)|
9.5 ± 0.36
|0.17||34.0 ± 0.59|
|7.5 ± 0.22||0.13||29.8 ± 0.70|
|Buds||6.5 ± 0.09||0.12||26.2 ± 1.68|
|Twigs||5.7 ± 0.10||0.11||23.5 ± 1.15|
The Gambel oak type of the Intermountain West provides good winter habitat for mule deer and offers high cover potential . However, tall, dense stands of Gambel oak provide poor winter ranges for deer and elk. Tall Gambel oak reaches beyond browse height of deer and elk and leads to shade-induced suppression of forbs and grasses . Dense stands may also exclude some big game animals. In White River Plateau, Colorado, Boyd  observed Gambel oak densities exceeding 51% canopy cover, which physically excluded elk.
The degree to which Gambel oak provides cover for wildlife species is as follows  :
|Small nongame birds||Good||Good||Good|
|Upland game birds||Good||Good||Good|
Gambel oak has not been used extensively for environmental rehabilitation of disturbed sites. The majority of research has been centered toward control or eradication. However, Gambel oak has a moderate value for long-term revegetation. The extensive root system helps provide soil stability and reduce erosion .
Propagation of Gambel oak using stem cuttings has shown little success [92,179]. Sopp  recommends stratification of Gambel oak seeds for 2 weeks at 35.6 degrees Fahrenheit (2 o C) to obtain maximum germination results. Sopp also recommends disinfecting acorns to prevent contamination by pathogens.
Native Americans of the Southwest used Gambel oak acorns for food .
Silviculture: Effective management of Gambel oak forests requires methods to assess current stand conditions and predict changes in relation to treatments imposed.
Several studies provide evidence regarding Gambel oak's ability to suppress other plant species. Allelopathic toxins produced by Gambel oak may limit the natural regeneration ability of ponderosa pine seedlings , but research results are limited. As an understory component of a ponderosa pine forest in central Arizona, Gambel oak did not limit the growth of overstory ponderosa pine . Gambel oak suppresses herbaceous species in open rangeland .
Density of Gambel oak stems within a stand is significantly (p < 0.05) related to stand height. According to McKell  and Brown , young Gambel oak thickets are generally dense, but thin out with age. Stand characteristics for Gambel oak between 6,890 and 8,200 feet (2,100-2,500 m) receiving annual precipitation of 14 to 20 inches (360-510 mm) in Utah were evaluated. As stand height increased, stem density decreased. A summary of stand characteristics is given below :
|Density/ha||Mean stem diameter (mm)||Range of stem diameter (mm)||Mean stem height (m)||Range of stem height (m)||Mean stem age (year)||Range of stem age (year)|
Stand height is not directly related to age. Stands with stems up to 142 years old produced trees similar in height to stands 1/3rd to 2/3rds as old. The same study found that lignotubers compromised 72% of the total belowground biomass of Gambel oak .
In general, heavy logging of ponderosa pine favors Gambel oak . Clearcutting of a ponderosa pine overstory in a forest with a Gambel oak and alligator juniper understory was evaluated 23 years later. Gambel oak stocking had increased 1.5 times, mostly in the form of vegetative sprouts, with regeneration averaging 1,090 ± 167 stems per acre. Clearcutting resulted in establishment of a Gambel oak-brushfield in what was previously a ponderosa pine forest . Gambel oak consistently sprouted adjacent to slash windrows in a ponderosa pine clearcut in Arizona .
Chojnacky [31,32] provides volume equations for Gambel oak in Arizona. Hutchings and Lamar  provide equations to estimate Gambel oak yields from foliage cover and basal area on various range sites in Utah.
An evaluation of snag density and composition on 2 national forests in Arizona reported that Gambel oak contributed 18% of snags in ponderosa pine forests, with ponderosa pine contributing 76.4% (alligator juniper was 2.3%). Within mixed-conifer forests Gambel oak contributed 24.3%, with white fir (Abies concolor) at 25.1%, ponderosa pine at 4.9%, and quaking aspen at 8.3% .
Inonotus andersoni is a fungus with the ability to girdle Gambel oak and kill the cambium. Although Inonotus andersoni is a functional member of Gambel oak habitats, it does not pose a major threat. Decay is a slow process most often occurring in older trees and does not seriously affect regeneration. Wildlife habitat is created through fungal-induced snags and live trees with snag characteristics .
A rotational fuel wood harvest cycle of 65 years allows Gambel oak clones to grow stems greater than the minimum fuel wood size of 3.5 inches (8.8 cm) in north-central Utah .
Soil ecology: Gambel oak places a heavy draw on soil moisture both within oak thickets and in open areas between oak thickets. Tew  observed soil moisture utilization by Gambel oak in northern Utah. An oak stand of 65 square foot basal area/acre (6 m2/ha) used 11 to 13 inches (28-33 cm) of water per year from the upper 8 feet (2 m) of soil. Initial water uptake occurs within the upper 4 feet (1.2 m) with additional water removed from the 4 to 8 foot (1-2 m) zone . In northern Arizona Gambel oak was more effective at avoiding soil water stress and atmospheric water stress than old- growth ponderosa pine . A comparison of mean soil moisture content (%) among 4 Gambel oak rangeland sites in southwestern Colorado was conducted over the course of 3 years. Results show higher soil moisture content (%) within herbicide controlled oak rangelands :
|Soil depth (ft)||Open areas between oak thickets||Oak thickets||Herbicide- controlled oak|
Leaf litter produced by Gambel oak has a positive effect on soil nitrogen within the surface (upper 5.9 inches (15 cm) of soil) [113,114]. Gambel oak leaves contain 2 to 4 times the N, P, S, Ca, Mg, and K of pine needles. Leaves also contain 8% less C than ponderosa pine needles. Gambel oak enhances nutrient release of ground cover within ponderosa pine stands by decaying faster than ponderosa pine litter. Presence of oak leaf litter may alter the distribution of nutrients within ponderosa pine forest floors .
The C:N ratio in ponderosa pine forest litter decreases when Gambel oak is a member of the understory compared to ponderosa pine without Gambel oak . A comparison of nutrients between freshly fallen Gambel oak leaves and ponderosa pine needles from trees growing side by side shows significantly higher nutrient content in Gambel oak litter :
|Nutrient (g/kg)||ponderosa pine||Gambel oak||Significance (p-value)|
Grazing: Beef production per acre is much greater in Gambel oak-controlled pastures than in pastures with no Gambel oak control. In southwestern Colorado herbicides have been used to decrease Gambel oak and increase livestock productivity . In general, cattle are safe from poisoning if other forage is available. Cattle should not be released when hungry on Gambel oak ranges with little forage other than oak .
Jefferies  found greater herbage production of needle-and-thread (Hesperostipa comata), western wheatgrass (Pascopyrum smithii), and blue grama (Bouteloua gracilis) in openings between oak stands than under Gambel oak canopies in both grazed and protected pastures. Kentucky bluegrass (Poa pratensis) had greater production under canopy than in the open . Seeding of Gambel oak rangeland in Utah should occur in the fall, just before leaf fall. Stevens and Davis  recommend aerial seeding followed with mechanical disturbance. Further information including a summary of recommended species, depending upon community type, is found in Stevens and Davis .
Gambel oak is most susceptible to insect herbivory early in the growing season, with young expanding leaves preferred . Gambel oak leaves support a higher insect biomass per unit of foliage than ponderosa pine .
Control methods: Top-kill of Gambel oak promotes vegetative sprouting. Numerous studies document the sprouting ability of Gambel oak after mechanical crushing  or herbicide treatment [59,92,98,139]. In general, the best strategy for reducing vigor of sprouting species is to apply control methods during periods of low carbohydrate reserves . However, total eradication of Gambel oak is rare due to prolific vegetative regeneration from roots, rhizomes and basal stems . Most control options provide short-term benefits that eventually produce Gambel oak thickets .
Control of Gambel oak with herbicides is extremely variable depending upon growing season and herbicide used. Herbicides may induce prolific sprouting, producing rangelands of lower quality than the original stand . The herbicide application rates of picloram, 2,4-D, or 2,4,5-T necessary to control Gambel oak kill most desirable shrubs and forbs. Fenuron kills Gambel oak but is persistent, producing a soil sterilization effect and a subsequent elimination of desirable plants . Effective control can be obtained from a mixture of picloram and 2,4,5-TP . Picloram pellets are an ineffective control for Gambel oak [45,46].
Application of hormone-type herbicides is recommended before full leaf stage or in late August before the end of fall regrowth corresponding to downward translocation. August applications, however, may be less effective due to wax accumulations on existing mature leaves . Applications corresponding with downward assimilate translocation maximize herbicide concentrations in the underground parts, where effective plant damage occurs .
Lauver and others  suggest integrated management for optimum control of Gambel oak. High application rates and high treatment costs are usually required for herbicide control of Gambel oak . Thinning programs, when conducted correctly, promote growth of remaining Gambel oak stems (not resprouts) allowing forage increases .
Combined with other nutritious forage low in tannin content, Gambel oak provides a healthy diet for domestic goats . When domestic goat browsing was initiated in late spring with periods of high intensity short duration grazing throughout the growing season in Northern Utah, Gambel oak showed a 78% reduction after 2 successive years .
When Gambel oak is abundant, domestic goats may prefer it to other available browse. Davis and others  provide several management considerations for obtaining maximum oak control from goats: all oak brush foliage should be accessible; time of goat browsing should center around late June (full leaf stage) and August (late summer regrowth); stocking rates of 5 to 10 goats per acre are preferred .
Wildlife: Kufeld  recommends fall prescribed burns rather than chaining or spraying to manage Gambel oak brush rangelands for elk, deer and cattle. Domestic goats were found to reduce the amount of Gambel oak browse available to wintering deer in Utah. Deer responded with greater consumption of sagebrush (Artemisia spp.) and rabbitbrush (Chrysothamnus spp.) . A detailed description of the management of Gambel oak associations for wildlife and livestock was prepared by Steinhoff .
Gambel oak occurs as clones  of shrubs in dense patches 3 to 20 feet (0.91-6.1 m) tall, often with a central thicket rising above the others , and as widely dispersed trees  up to 75.5 feet (23 m) tall . Clones show uniform characteristics in shape, pubescence, and color . Variability in life form corresponds with relative levels of water stress; stunted shrubs are present on xeric sites with moderate-sized trees found in wetter locations [54,107]. Gambel oak bark ranges from 0.5 to 0.75 inch (1.2-1.9 cm) thick. The bark is deeply divided into broad, irregular, often connected, flat ridges. Branches are slender and coated with short, pale, rust-colored hairs when 1stappearing . Leaves of Gambel oak are highly variable, differing in outline, texture, lobing [13,92], pubescence, and size. Acorns are sessile or pedunculate , with an oval shape, usually 0.75 inch (1.9 cm) long and 0.63 inch (1.6 cm) broad .
The underground system of Gambel oak consists of a lignotuber with deep-feeding roots . Lignotubers possess many scattered adventitious buds  .Clones are interconnected with rhizomes  that intertwine with lignotubers. Root grafting is common; root-endomycorrhizal associations may also occur .
The growth rate of Gambel oak may vary with age. Barger and Ffolliott  report Gambel oak grows rapidly in height and diameter at early stages of life, with growth rates steadily declining with age. In contrast, in central Utah study Wagstaff  observed little change in growth rate of Gambel oak diameter during the 1st 100 years of life.
Ecological characteristics compiled by Loehle , are summarized below:
|Typical age of mortality (years)||Maximum Longevity (years)||Specific gravity||Relative growth rate||Relative Decay Resistance|
Seed: Production of mature flowers is directly related to moisture availability. Xeric sites often fail to produce mature female flowers, yet male catkins are produced in abundance. On moist sites, flowers of both sexes are produced in large numbers . Acorn production in Arizona was directly related to moisture availability, averaging 188,000 mature acorns/acre (464,548/ha) and over 331,000 per acre (817,900/ha) in heavy moisture years . Although Gambel oak generally possesses distinct male and female inflorescences on a single plant, Tucker and others  observed an inflorescence containing both anthers and pistils in Utah. The following year strictly monoecious flowers were produced. Female flowers are found throughout the Gambel oak canopy while male flowers are almost exclusively located at the top .
Extent of acorn production is also related to stem diameter. Few acorns are produced from stems less than 2 inches (5.1 cm) diameter breast height (d.b.h.), and production rapidly declines when stems are greater than 14 inches (35.6 cm). Maximum acorn production occurs from stems 12 to 14 inches (30.5-35.6 cm) d.b.h. [142,171]. Throughout Utah, 4 to 6 months are required to produce mature acorns [42,92]. Spring freezing may reduce acorn production .
Gambel oak may occur at high elevations, where a 60- to 90-day growing season exists. Although at high-elevation ranges the growing season is too short to produce mature acorns, expansion occurs through vegetative reproduction . Limited colonization of the higher-elevational range is thought to be a function of the short growing season .
Overall effectiveness of reproduction through seed is directly related to moisture availability . Seedlings are more common in the southern range of Gambel oak , where summer rains are heavy and more frequent . Fewer seedlings are found in the northern range [150,155,157]. Neilson  found seedling establishment directly relating to consistently high presence of soil moisture. Persistent mesic conditions provide the best conditions for seedling survival. Greater survivorship in winter and summer is also associated with closed canopies .
Colonization through seed is enhanced by avian and small mammal acorn dispersal. Acorns of Gambel oak are dispersed by rodents and birds . Band-tailed pigeons, scrub jays, Steller's jays, Lewis woodpeckers, and acorn woodpeckers are agents of dispersal [33,91,92]. The Utah rock squirrel regularly provides short-distance acorn dispersal .
Vegetative: Gambel oak has strong vegetative reproduction capabilities. In most of its range, Gambel oak regeneration depends more on sprouting than establishment from seed . The large underground structure of Gambel oak supports rapid and extensive sprouting following top removal . In Utah vegetative spread of Gambel oak thickets averaged 4-inches (10 cm) per year, with lows of 1.5 inches (3.8 cm) and a high of 12 inches (30.5 cm) . Vegetative reproduction occurs through adventitious buds on lignotubers  and freely branched rhizomes . A large difference in ability to regenerate by cloning exists between the southern and northern range of Gambel oak. In Arizona and New Mexico, groupings usually consisted of 1 to 7 ramets per clone  compared to 100 to 1,000 ramets per clone observed in the north [26,169].
The distribution of adventitious buds and rhizomes (in cm) within the soil profile of a Gambel oak stand in central Utah was as follows :
Adventitious buds were concentrated in the top 11.8 inches (30 cm) of soil. More adventitious buds were found on lignotubers than on rhizomes . Lignotubers provide the primary source for regeneration after top-kill; rhizomes possess fewer buds and facilitate widespread development of clones .
The upper and lower limits of Gambel oak's range are established by the Arizona monsoons that generates a gradient of increasing cold stress in winter and spring and a summer drought stress with increasing latitude . Gambel oak prefers a mean annual temperature of 44.6 to 50 degrees Fahrenheit (7-10 oC) with winter temperatures below negative 0.4 degrees Fahrenheit (-18 oC) . Gambel oak does not occur in areas where winter precipitation falls below 10 inches (250 mm) or where subfreezing temperatures persist for long periods of time . Annual mean precipitation measured over 14 years (1934 to 1948) at 7,655 feet (2,333 m) within Gambel oak habitats of the mountain brush zone was 20.10 inches (510 mm) . Throughout its distribution Gambel oak occurs between 3,250 and 10,200 feet (990-3,110 m) . Elevation limits are the widest at the southern extent, narrowing northward . A preference for south slopes was observed between 8,200 and 8,700 feet (2,500-2,650 m) in southwestern New Mexico . At 7,500 to 8,000 feet (2,286-2,438 m) in Mount Livermore, Texas, Gambel oak occurs on ledges and bordering talus slopes .
Several environmental parameters were evaluated in Gambel oak stands, comparing understory and open areas between oaks in the lower Unita mountains, Utah. Elevation is 7,218 feet (2,200 m); slope is 10% with an 185o exposure. Mean annual precipitation is 17.7 inches (450 mm), 60% of which is received in winter . Litter was deeper, shrubs had greater cover, and light was less intense under Gambel oak:
|Litter depth (cm)||2.3||0.2|
|Perennial forbs (%)||15.6||27.4|
|Light intensity1 (foot candles)||76||242|
Elevational ranges of Gambel oak are:SUCCESSIONAL STATUS:
Canopy suppression is a successional trend when Gambel oak is associated with bigtooth maple, white fir, ponderosa pine, Rocky Mountain juniper, or Colorado pinyon [34,36,56,71,96,143,159]. Across its range, Gambel oak occupies a seral, postfire successional stage with late successional associates more susceptible to fire [22,62,214].
Gambel oak is listed as a persistent seral stage in the ponderosa pine of northern Arizona, with he majority of Gambel oak occurring as trees. Populations of Gambel oak increase with disturbance in ponderosa pine woodlands .
In southern and southwestern Colorado, Gambel oak occupies a secondary successional stage in ponderosa pine and Douglas-fir (Pseudotsuga menziesii) stands removed by fire or logging [26,93]. It is a persistent subclimax to conifers or a climax species of foothill ranges [56,59,96,134].
Mountain brush vegetation where Gambel oak and bigtooth maple are codominant tend to develop into a bigtooth maple-dominated brush type. The successional transition to a bigtooth maple dominant overstory is attributed to the greater reproductive potential and shade tolerance of bigtooth maple . Within Gambel oak-bigtooth maple brush, bigtooth maple seedlings grow readily under and on the periphery of bigtooth maple and Gambel oak canopies. Gambel oak seedlings are rarely observed under dense bigtooth maple canopies . Bigtooth maple successfully invaded Gambel oak brush in the Wasatch Mountains of Utah, while Gambel oak had difficulty invading bigtooth maple stands .
In central Utah, Gambel oak/bigtooth maple brush communities at 6,500 to 7,800 feet (1,981-2,377 m) may succeed to conifer-pinyon-juniper at the low elevations and to white fir at upper elevations .
Gambel oak flowers usually appear in late March to early April with acorns ripening in August or September . In Utah, flowers appear when leaves are nearly half grown, usually May or June ; at the lower elevation limits in Utah, flowers occasionally appear in early May [28,200]. Acorns mature in northern Utah from September to early October . The following table provides a summary of Gambel oak seasonal development during a 160 to 175 day growing season at 7,655 feet (2,333 m) in northern Utah :
|Flower buds bursting||Leaf buds bursting||In full leaf||In full bloom||Fruit ripe||Fruit dropped|
|May 25||May 23||June 17||June 5||September 25||October 10|
Gambel oak produces buds in winter for the following spring. Not all buds produced in winter become active; some dormancy is maintained. Dormant buds may become active if new shoots are defoliated .
In southwestern Colorado, at least 5 weeks are required after snowmelt before onset of spring growth. Photoperiod requirements prevent bud burst occurring earlier than the 3rd week of May. Shoot elongation is generally 24 to 27 days and is not dependent upon date of bud burst .
Fire frequency within Gambel oak stands varies with plant associates. In most associations, little fuel is available for fires to occur in successive growing seasons [44,144]. Pure Gambel oak stands in southwestern Colorado burn most readily between October 1 and snowfall, when dead leaves remain on branches and the National Fire Danger Rating System burning index is between 40 and 75 . Fall fires carry most readily through pure Gambel oak stands after leaf senescence but before leaf fall . Dry, windy weather readily spreads flames through oak crowns . Gambel oak stands burn well during dry summer conditions, especially on steep, south aspects [22,142].
Fire succession: Fire in Gambel oak stands may promote a brief grass-forb stage depending upon fire intensity and frequency . In most situations, Gambel oak resprouts vigorously the 1st growing season following fire [13,26,44,53,76,143,144]. If successive fires occur at this stage, Gambel oak stands may be reduced to a grass-forb stage [44,144]. Repeated fires in Gambel oak ranges may deplete stored resources of rhizomes and lignotubers . As sprouts continue to grow, natural thinning occurs, adding dead stems to the fuel. Fire occurring at this stage also sends Gambel oak stands back to a seral grass-forb stage. In absence of fire, sprouts form young poles. At this stage fires are stand replacement, either creating openings within stands for colonization by resprouts or a complete recycling back to a grass-forb stage. In the absence of fire, Gambel oak stands reach maturity in 60 to 80 years. Fire response in mature stands is similar to that in young poles. A severe fire will recycle the stand; low-severity fires create openings for resprouts. At 80 years Gambel oak stems die naturally, creating more openings for sprouts .
The Utah woodlands at 5,500 to 7,800 feet (1,676-2,377 m), where Gambel oak and/or bigtooth maple are dominant, codominant, or long-term seral dominants, have low combustibility. However, environmental conditions occasionally permit severe wildfires . Gambel oak leaves killed by a late spring freeze may provide dried tinder during summer or early fall . With increasing bigtooth maple cover, fire susceptibility lessens through relatively rapid decomposing leaf litter and a reduced understory . Susceptibility increases where conifers are encroaching, due to resinous foliage and persistent litter .
Fire in ponderosa pine stands of Arizona may convert stands to thickets of Gambel oak , initiating a Gambel oak successional stage after the competing ponderosa pine overstory is removed [44,53]. Dense understories of Gambel oak may serve as ladder fuels that carry fire to overstory tree crowns, increasing fire risk to ponderosa pine . A detailed description of fire-induced succession within ponderosa pine-Gambel oak habitat types can be found in Crane .
In Zion National Park, Utah, fires are more frequent in ponderosa pine stands with a Gambel oak understory than in Gambel oak-dominated stands without ponderosa pine litter . The mean historical fire return interval in ponderosa pine-Gambel oak forests near Tucson, Arizona, was 3.7 years between 1637 and 1883. Only a single fire scar was recorded between 1883 and 1951. With fire exclusion, Gambel oak and ponderosa pine densities have increased. A reconstruction of 1883 presettlement forest structure compared with contemporary forest structure from a 1994/1995 inventory at Camp Navajo, Arizona, is summarized below :
|Species||Presettlement mean||Contemporary mean|
|Basal area (m2/ha)|
Gambel oak is a seral species in quaking aspen, pinyon-juniper, and mixed-conifer forests . Gambel oak occupies a seral postfire successional stage in pinyon-juniper woodlands [61,218]. Reestablishment of pinyon pine and most juniper species after disturbance is dependent entirely upon seed production. The vegetative reproductive capabilities of Gambel oak provide it with an inherent postfire advantage. Gambel oak occupies a seral postfire stage within pinyon-juniper woodlands of Mesa Verde, Colorado. Gambel oak dominates for approximately 25 postfire years, and may persist up to 100 years before canopy suppression by pinyon pine and juniper species . Floyd  presents the Gambel oak vegetation type as successional in Colorado, altering the habitat and facilitating invasion and eventual succession to pinyon-juniper woodland. Within Douglas-fir forests of the White Mountains of Colorado, Hanks and Dick-Peddie  describe Gambel oak as occupying a postfire successional stage that may persist up to 100 years before being shaded out by coniferous overstory. Within the Huachuca Mountains of Arizona, Gambel oak was found in Douglas-fir communities after fire. As Gambel oak matured, Douglas-fir seedlings occupied the understory, suggesting eventual return to Douglas-fir dominance . Hypothetical postfire succession in Rocky Mountain habitats where Gambel oak occurs is described by Crane .
Find fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find Fire Regimes". The following table provides fire-return intervals in some communities where Gambel oak occurs :
|Community or Ecosystem||Dominant Species||Fire Return Interval Range (years)|
|mountain-mahogany-Gambel oak scrub||Cercocarpus ledifolius-Quercus gambelii||< 35 to < 100|
|western juniper||Juniperus occidentalis||20-70|
|Rocky Mountain juniper||J. scopulorum||< 35 |
Tree with adventitious bud/root crown/soboliferous species root sucker
Tall shrub, adventitious bud/root crown
Secondary colonizer (on-site or off-site seed sources)
Fire may top-kill Gambel oak . Gambel oak habit and community structure affect susceptibility to fire. Tree forms are less likely to be top-killed in a low-severity fire compared to shrubs with branches closer to the burning surface fuels .
Fire usually stimulates sprouting of Gambel oak after top-kill [13,26,53,76,143], increasing density of previously open stands and merging scattered stands into continuous thickets . Gambel oak regeneration after fire is usually vigorous . Sprouts may be observed within 10 postfire days .
Seed: Caches of acorns gathered by rodents are a source of postfire regeneration .
Sprouting: First-year responses to fire show vigorous Gambel oak regrowth. Adventitious buds located on rhizomes and lignotubers may produce stems reaching up to 18 inches (45.7 cm) in height. Surviving stems also resprout from buds . Dormant buds on rhizomes are stimulated by fire . Rhizomes generally lie between 4 and 20 inches (10-50 cm) below soil surface, so they are protected from all but the most severe fires . Wright  predicts continued growth after fire in Gambel oak, inducing a natural thinning of continuous thickets that ultimately decline to coverage equaling the previously unburned stand within 18 years.
Postfire stand recovery time varies according to fire severity, climatic factors, and site characteristics. Recovery after fire is fastest on warm, south-facing slopes at low elevations .
Postfire regrowth was greatest the 1st year following a summer (July) and fall (September to October) fire between 4,600 and 6,400 feet (1,402-1,950 m) in northern Utah. August 1 postfire growth was 16 to 18 inches (41-46 cm), with 2nd-year growth at 4 to 8 inches (10-20 cm) . Other studies show similar, rapid Gambel oak recovery from fire. New shoots with flowers were produced 26 days after an August fire in Orem Park, Provo Canyon, Utah, on stems that were defoliated but not killed . Gambel oak shrublands were nearly half-covered with resprouting oaks 1 year after an August fire in Mesa Verde National Park, Colorado . Also in Mesa Verde National Park, Gambel oak crown sprouted and leafed within a few months after a mid-July to August lightning-ignited wildfire at 7,500 feet (2,286 m) . Resprouting of Gambel oak after an October prescribed burn in Grand Mesa National Forest, Colorado, was greatest at the 1st postburn growing season, decreasing the 2nd and following growing seasons.
In mature Gambel oak stands ( > 60 years), severe fires top-kill all or most of the stand; low-severity fires create openings for sprouts .
Gambel oak leaf moisture content varies greatly from year to year. Moisture content decreases from May to August ; August foliage has less than half the moisture of May foliage . Within Waterton Canyon, Colorado, the moisture content of Gambel oak leaves decreased significantly (p < 0.001) in both the upper and lower canopy from May to August. This was true regardless of aspect and elevation. Ogle  constructed a model to predict fire behavior in relation to fuel moisture in Gambel oak.
Gambel oak produces a large amount of leaf litter that contributes, in most cases, 70% of total stand litter. In Utah, accumulated litter biomass of approximately 33,335 pounds per acre (37,348 kg/ha) was about equivalent to the bole biomass of 36,328 pounds per acre (40,702 kg/ha) .
The distribution of belowground nitrogen (kg/ha) and the percent of total belowground nitrogen was evaluated in a Gambel oak stands near Ephraim, Utah :
|Aboveground||kg/ha||% of N capital|
Based on this data, harvest followed by broadcast burning may result in a 10% loss in nitrogen capital depending upon fire intensity .
Fire alters the plant community in which Gambel oak occurs. Gambel oak communities are usually tolerant of fire, but herbage yields of associated species do not appear to improve . Frequency and cover of major plant species on Gambel oak-dominated sites in oak brush near Wasatch Mountains State Park, Utah, were evaluated 1 year after an August wildfire :
|Species||Frequency (%)||(%)||Frequency (%)||Cover (%)|
|pale agoseris (Agoseris glauca)||11.8||1.06||0.90||< 0.01|
|Saskatoon serviceberry (Amelanchier alnifolia)||23.50||1.09||8.1||0.95|
|China aster (Callistephus chimensis)||5.90||0.03||0||0|
|lambsquarters (Chenopodium album)||0||0||24.30||1.24|
|narrowleaf goosefoot (C. leptophyllum)||5.90||0.03||19.8||0.39|
|maiden blue-eyed Mary (Collinsia parciflora)||29.40||0.15||27.9||0.32|
|tapertip hawksbeard (Crepis acuminata)||47.10||1.38||3.60||0.02|
|Brown's pea (Lathyrus spp.)||58.80||2.59||7.20||0.30|
|biscuitroot (Lomatium triternatum)||35.30||0.77||1.8||0.01|
|tansyaster (Machaerantera canescens)||0||0||0.9||0.03|
|bushy knotweed (Polygonum ramosissimum)||0||0||6.3||0.03|
|threeawn goldenrod (Solidago velutina)||0||0||2.7||0.19|
|mullein (Verbascum thapsus)||0||0||19.8||1.2|
|goldeneye (Heliomeris multiflora)||0||0||24.3||0.86|
Control: Fall burning provides the least amount of Gambel oak control. Gambel oak is dormant in the fall and total nonstructural carbohydrate reserves are at their peak . Gambel oak is most severely harmed by successive fires when carbohydrate reserves are low. Top-killing Gambel oak in the summer may produce resprouts within 6 weeks. However, by fall, resprouts are still immature and carbohydrate recovery cannot begin until the following spring leaf-out, producing a 9- to 10-month period without carbohydrate replacement. Control may occur though carbohydrate stress imposed by 2 summer burns. However, effective burning may require biennial treatments due to light litter accumulation within a single growing season .
Observations within a ponderosa pine stand in southwestern Colorado at 7,600 feet (2,316 m) suggest frequent burning during mid-August provides control for Gambel oak. Vigorous Gambel oak sprouting was observed regardless of burn season. Twice-burned spring and fall treatments resulted in resprout densities equal to once-burned areas. Twice-burned summer treatments resulted in decreased oak density, frequency, and cover. Resprouts after twice-burned summer treatments were confined to top-killed oak thickets; sprouting after fall and spring burns was not restricted; and previous Gambel oak thicket boundaries were extended. Frischknect and Plummer  suggest seeding competitive grasses after fire, but additional studies are required to substantiate findings .
Harrington, M. G. 1982. Stand, fuel, and potential fire behavior characteristics in an irregular southeastern Arizona ponderosa pine stand. Res. Note RM-418. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 6 p. .
Harrington, M. G. 1985. The effects of spring, summer, and fall burning on Gambel oak in a Southwestern ponderosa pine stand. Forest Science. 31(1): 156-163. .
Fall 1977/fire severities not reported
The study was conducted on 2.5-acre (1 ha) plots within the San Juan National Forest in southwestern Colorado.
The study site consisted of a multiple-aged Rocky Mountain ponderosa pine overstory averaging 300 trees and 124 square feet (11.5 m2) basal area per acre. There was a dense Gambel oak (Quercus gambelii) understory. Herbaceous and other shrubby understory vegetation was sparse.  The majority of Rocky Mountain ponderosa pine (75%) occurred as trees in the 4- to 11-inch (10-28 cm) d.b.h. class. In forest openings, Gambel oak reached heights of 15 feet (4.8 m) with 4-inch (10 cm) basal diameters. The majority of Gambel oak was less than 4 feet (1.2 m) tall and 2 inches (5 cm) in basal diameter.
|full leaf stage||2nd growth period||dormant, near peak root carbohydrate levels|
Burned areas were located on a south aspect with less than 5% slope at 7,600 feet (2,316 m). Average annual precipitation in Mancos, Colorado, 5 miles southwest of the study site is 17 inches (430 mm), with the least amount of precipitation occurring in June and the greatest amount in August. Fire has not occurred since 1877. Before 1877 fire intervals were 1 to 16 years with an average of 6 years.
|Wind speed (mph)||2-5||1-6||1-5|
|Spread rate (ft/min)||6||8||5|
|Flame length (ft)||3.0||3.5||3.5|
|Wind speed (mph)||1-3||2-7||2-6|
|Spread rate (ft/min)||3||10||6|
|Flame length (ft)||1.0||3.5||3.0|
Fuels were dry during the 2nd spring burn, resulting in rapid-fire spread that consumed 35% of the forest floor fuels. Nearly all the new litter was consumed, along with 10% of the residual fuels. The summer burn consumed 17% of the forest floor, 70% of which was new litter.
Single-burn treatments resulted in 100 to 150% increases in Gambel oak density and a 10 to 40% increase in frequency. Cover of Gambel oak was only reduced temporarily. Reductions 1 year after the initial burns were as follows:
|Oak d.b.h (in)||Reduction (%)||Reduction numbers (stems/200 ft2)|
Overall cover of Gambel oak was reduced 20 to 35% 1 year after the initial burn. Cover of fall and spring burn plots equaled those of control plots 2 years after the burn.
Consecutive fall and spring burns resulted in slight increases in Gambel oak sprouts with successive summer burns reducing Gambel oak density by 20%, frequency by 16%, and cover by 12%. Gambel oak frequencies after the twice-burn spring and fall treatments increased 10% by postfire year 4. Cover of the twice-burned plats was reduced, particularly on the summer treatment. However, all treatments had slight Gambel oak cover increases by postfire year 4.
Single burns in any season are unlikely to remove Gambel oak from ponderosa pine understories. However, results of this study suggest consecutive summer burns reduce Gambel oak populations. Gambel oak burned during the summer regrowth period, when carbohydrate levels are reduced, is unable to sprout and accumulate carbohydrates before fall dormancy. Successive burns in this period can place additional stress on Gambel oak. Spring burns generally allow good recovery prior to dormancy. Similarly, fall burns after carbohydrate reserves are accumulated have little effect on Gambel oak.
The deep-rooted Gambel oak can compete effectively with ponderosa pine for available water and nutrients. When Gambel oak sprouts prolifically after fire or other disturbance, it is capable of inhibiting ponderosa pine regeneration. Consecutive burns in ponderosa pine-Gambel oak stands could, in time, favor the growth and regeneration of pine.
1. Abrams, Marc D. 1990. Adaptations and responses to drought in Quercus species of North America. Tree Physiology. 7(1-4): 227-238. 
2. Aguilar, Jeffrey M.; Boecklen, William J. 1992. Patterns of herbivory in the Quercus grisea X Quercus gambelii species complex. Oikos. 64: 498-504. 
3. Alexander, Billy G., Jr.; Fitzhugh, E. Lee; Ronco, Frank, Jr.; Ludwig, John A. 1987. A classification of forest habitat types of the northern portion of the Cibola National Forest, New Mexico. Gen. Tech. Rep. RM-143. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 35 p. 
4. Alexander, Billy G., Jr.; Ronco, Frank, Jr.; Fitzhugh, E. Lee; Ludwig, John A. 1984. A classification of forest habitat types of the Lincoln National Forest, New Mexico. Gen. Tech. Rep. RM-104. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 29 p. 
5. Alexander, Billy G., Jr.; Ronco, Frank, Jr.; White, Alan S.; Ludwig, John A. 1984. Douglas-fir habitat types of northern Arizona. Gen. Tech. Rep. RM-108. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 13 p. 
6. Alexander, Robert R. 1987. Classification of the forest vegetation of Colorado by habitat type and community type. Res. Note RM-478. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 14 p. 
7. Alexander, Robert R. 1988. Forest vegetation on National Forests in the Rocky Mountain and Intermountain Regions: habitat and community types. Gen. Tech. Rep. RM-162. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 47 p. 
8. Alexander, Robert R.; Hoffman, George R.; Wirsing, John M. 1986. Forest vegetation of the Medicine Bow National Forest in southeastern Wyoming: a habitat type classification. Res. Pap. RM-271. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 39 p. 
9. Alexander, Robert R.; Ronco, Frank, Jr. 1987. Classification of the forest vegetation on the National Forests of Arizona and New Mexico. Res. Note RM-469. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 10 p. 
10. Allman, Verl Phillips. 1953. A preliminary study of the vegetation in an exclosoure in the chaparral of the Wasatch Mountains, Utah. Utah Academy Proceedings. 30: 63-78. 
11. Anthony, Robert G.; Smith, Norman S. 1977. Ecological relationships between mule deer and white-tailed deer in southeastern Arizona. Ecological Monographs. 47: 255-277. 
12. Austin, Dennis D.; Urness, Philip J.; Riggs, Robert. 1986. Vegetal change in the absence of livestock grazing, mountain brush zone, Utah. Journal of Range Management. 39(6): 514-517; 1986. 
13. Baker, William L. 1949. Soil changes associated with recovery of scrub oak, Quercus gambelii, after fire. Salt Lake City, UT: University of Utah. 65 p. Thesis. 
14. Barger, R. L.; Ffolliott, P. F. 1972. Physical characteristics and utilization of major woodland tree species in Arizona. Res. Pap. RM-83. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 80 p. 
15. Beaulieu, Jean Thomas. 1975. Effects of fire on understory plant populations in a northern Arizona ponderosa pine forest. Flagstaff, AZ: Northern Arizona University. 38 p. Thesis. 
16. Berg, A. R.; Plumb, T. R. 1972. Bud activation for regrowth. In: McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., tech. eds. Wildland shrubs--their biology and utilization: An international symposium: Proceedings; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 279-286. 
17. 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. 
18. Betters, David R. 1983. Overstory-understory relationships: aspen forests. In: Bartlett, E.T.; Betters, David R., eds. Overstory-understory relationships in western forests. Western Regional Research Publication No. 1. Fort Collins, CO: Colorado State University Experiment Station: 5-8. 
19. Biondi, Franco; Klemmedson, James O.; Kuehl, Robert O. 1992. Dendrochronological analysis of single-tree interactions in mixed pine-oak stands of central Arizona, USA. Forest Ecology and Management. 48: 321-333. 
20. Bowers, Janice E.; McLaughlin, Steven P. 1987. Flora and vegetation of the Rincon Mountains, Pima County, Arizona. Desert Plants. 8(2): 50-94. 
21. Boyd, Raymond J. 1970. Elk of the White River Plateau, Colorado. Technical Publication No. 25. Denver, CO: Colorado Division of Game, Fish and Parks. 126 p. 
22. Bradley, Anne F.; Noste, Nonan V.; Fischer, William C. 1991. Fire ecology of forests and woodlands in Utah. Gen. Tech. Rep. INT-287. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 128 p. 
23. Brady, Ward; Bonham, Charles D. 1976. Vegetation patterns on an altitudinal gradient, Huachuca Mountains, Arizona. The Southwestern Naturalist. 21(1): 55-66. 
24. Brian, Nancy J. 1992. Historical review of water flow and riparian vegetation at Walnut Canyon National Monument, Arizona. Tech. Rep. NPS/WRUA/NRTR-92/44. Tuscon, AZ: The University of Arizona, School of Renewable Natural Resources, Cooperative National Park Resources Studies Unit. 39 p. 
25. Britton, Carlton M.; Wright, Henry A. 1983. Brush management with fire. In: McDaniel, Kirk C., ed. Proceedings--brush management symposium; 1983 February 16; Albuquerque, NM. Denver, CO: Society for Range Management: 61-68. 
26. Brown, Harry E. 1958. Gambel oak in west-central Colorado. Ecology. 39(2): 317-327. 
27. Brown, James K.; Smith, Jane Kapler, eds. 2000. Wildland fire in ecosystems: effects of fire on flora. Gen. Tech. Rep. RMRS-GTR-42-vol. 2. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 257 p. 
28. Brown, Roy C.; Mogensen, H. Lloyd. 1972. Late ovule and early embryo development in Quercus gambelii. American Journal of Botany. 59: 311-316. 
29. Castetter, Edward F. 1935. Ethnobiological studies in the American Southwest. Biological Series No.4: Volume 1. Albuquerque, NM: University of New Mexico. 62 p. 
30. Chechowitz, Naomi; Chappell, Dorothy M. 1990. Morphological, electrophoretic, and ecological analysis of Quercus macrocarpa populations in the Black Hills of South Dakota and Wyoming. Canadian Journal of Botany. 68: 2185-2194. 
31. Chojnacky, David C. 1988. Juniper, pinyon, oak, and mesquite volume equations for Arizona. Res. Pap. INT-391. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 11 p. 
32. Chojnacky, David C. 1992. Estimating volume and biomass for dryland oak species. In: Ffolliott, Peter F.; Gottfried, Gerald J.; Bennett, Duane A.; [and others], technical coordinators. Ecology and management of oak and associated woodlands: perspectives in the southwestern United States and northern Mexico: Proceedings; 1992 April 27-30; Sierra Vista, AZ. Gen. Tech. Rep. RM-218. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 155-161. 
33. Christensen, Earl M. 1949. The ecology and geographic distribution of oak brush (Quercus gambelii) in Utah. Salt Lake City, UT: University of Utah. 70 p. Thesis. 
34. Christensen, Earl M. 1950. Distributional observations of oak brush (Quercus gambelii Nutt.) in Utah. Proceedings, Utah Academy of Sciences, Arts and Letters. 27: 22-25. 
35. Christensen, Earl M. 1955. Ecological notes on the mountain brush in Utah. Utah Academy Proceedings. 32: 107-111. 
36. Christensen, Earl M. 1958. Growth rates and vegetation change in the oak-maple brush in lower Provo Canyon, Utah. Proceedings of Utah Academy of Sciences, Arts, and Letters. 35: 167-168. 
37. Clary, Warren P. 1978. Producer-consumer biomass in Arizona ponderosa pine. Gen. Tech. Rep. RM-56. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 4 p. 
38. Clary, Warren P.; Tiedemann, Arthur R. 1986. Distribution of biomass within small tree and shrub form Quercus gambelii stands. Forest Science. 32(1): 234-242. 
39. Clary, Warren P.; Tiedemann, Arthur R. 1992. Ecology and values of Gambel oak woodlands. In: Ffolliott, Peter F.; Gottfried, Gerald J.; Bennett, Duane A.; [and others], technical coordinators. Ecology and management of oaks and associated woodlands: perspectives in the southwestern United States and northern Mexico: Proceedings; 1992 April 27-30; Sierra Vista, AZ. Gen. Tech. Rep. RM-218. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 87-95. 
40. Clary, Warren P.; Tiedemann, Arthur R. 1993. Bole volume growth in stems of Quercus gambelii. The Great Basin Naturalist. 53(2): 162-167. 
41. Coffman, Michael S. 1975. Shade from brush increases survival of planted Douglas-fir. Journal of Forestry. 73: 726-728. 
42. Costello, David F.; Price, Raymond. 1939. Weather and plant-development data as determinants of grazing periods on mountain range. Tech. Bull. 686. Washington, DC: U.S. Department of Agriculture. 31 p. 
43. Cottam, Walter P.; Tucker, John M.; Drobnick, Rudy. 1959. Some clues to Great Basin postpluvial climates provided by oak distributions. Ecology. 49(3): 361-377. 
44. Crane, Marilyn F. 1982. Fire ecology of Rocky Mountain Region forest habitat types. Final Report Contract No. 43-83X9-1-884. Missoula, MT: U.S. Department of Agriculture, Forest Service, Region 1. 272 p. On file with: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. 
45. Davis, E. A.; Gottfried, G. J. 1981. Response of New Mexico locust and Gambel oak to picloram pellets. In: Proceedings, Western Society of Weed Science: 1981 Research Progress Reports; 1981 March 17-19; San Diego, CA. [Place of publication unknown]: [Publisher unknown]. 54-55. 
46. Davis, E. A.; Gottfried, G. J. 1983. Picloram pellets control New Mexico locust sprouts on a cleared forest site in Arizona. Down to Earth. 39(1): 18-21. 
47. Davis, Gary G.; Bartel, Lawrence E.; Cook, C. Wayne. 1975. Control of Gambel oak sprouts by goats. Journal of Range Management. 28(3): 216-218. 
48. Davis, James N.; Welch, Bruce L. 1985. Winter preference, nutritive value, and other range use characteristics of Kochia prostrata (L.) Schrad. The Great Basin Naturalist. 45(4): 778-783. 
49. DeVelice, Robert L.; Ludwig, John A. 1983. Climax forest series of northern New Mexico and southern Colorado. In: Moir, W. H.; Hendzel, Leonard, tech. coords. Proceedings of the workshop on Southwestern habitat types; 1983 April 6-8; Albuquerque, NM. Albuquerque, NM: U.S. Department of Agriculture, Forest Service, Southwestern Region: 45-53. 
50. DeVelice, Robert L.; Ludwig, John A. 1983. Forest habitat types south of the Mogollon Rim, Arizona and New Mexico. Final Report. Cooperative Agreement No. 28-K2-240. Las Cruces, NM: New Mexico State University. 47 p. 
51. DeVelice, Robert L.; Ludwig, John A.; Moir, William H.; Ronco, Frank, Jr. 1986. A classification of forest habitat types of northern New Mexico and southern Colorado. Gen. Tech. Rep. RM-131. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 59 p. 
52. Dick, Brian L.; Urness, Philip J. 1991. Nutritional value of fresh Gambel oak browse for Spanish goats. Journal of Range Management. 44(4): 361-364. 
53. Dick-Peddie, W. A.; Moir, W. H. 1970. Vegetation of the Organ Mountains, New Mexico. Science Series No. 4. Fort Collins, CO: Colorado State University, Range Science Department. 28 p. 
54. Dina, Stephen J.; Klikoff, Lionel G. 1973. Carbon dioxide exchange by several streamside and scrub oak community species of Red Butte. The American Midland Naturalist. 89(1): 70-80. 
55. Dittberner, Phillip L.; Olson, Michael R. 1983. The plant information network (PIN) data base: Colorado, Montana, North Dakota, Utah, and Wyoming. FWS/OBS-83/86. Washington, DC: U.S. Department of the Interior, Fish and Wildlife Service. 786 p. 
56. Dixon, Helen. 1935. Ecological studies on the high plateaus of Utah. Botanical Gazette. 97: 272-320. 
57. Eastmond, Robert J. 1968. Vegetational changes in a mountain brush community of Utah during eighteen years. Provo, UT: Brigham Young University. 64 p. Thesis. 
58. Ehleringer, James R.; Arnow, Lois A.; Arnow, Ted; [and others]. 1992. Red Butte Canyon Research Natural Area: history, flora, geology, climate, and ecology. The Great Basin Naturalist. 52(2): 95-121. 
59. Engle, D. M.; Bonham, C. D.; Bartel, L. E. 1983. Ecological characteristics and control of Gambel oak. Journal of Range Management. 36(3): 363-365. 
60. Engle, David M.; Bonham, Charles D. 1980. Nonstructural carbohydrates in roots of gambel oak sprouts following herbicide treatment. Journal of Range Management. 33(5): 390-394. 
61. Erdman, James A. 1970. Pinyon-juniper succession after natural fires on residual soils of Mesa Verde, Colorado. Brigham Young University Science Bulletin: Biological Series. 11(2): 1-26. 
62. Erdman, James Allen. 1969. Pinyon-juniper succession after fires on residual soils of the Mesa Verde, Colorado. Boulder, CO: University of Colorado. 81 p. Dissertation. 
63. Erdman, Kimball S. 1961. Distribution of the native trees of Utah. Brigham Young University Science Bulletin: Biological Series. 11: 1-34. 
64. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. 
65. Faeth, Stanley H.; Rooney, Robert F., III. 1993. Variable budbreak and insect folivory of Gambel oak (Quercus gambelii: Fagaceae). The Southwestern Naturalist. 38(1): 1-8. 
66. Fairweather, M. L.; Gilbertson, Robert L. 1992. Inonotus andersonii: a wood decay fungus of oak trees in Arizona. In: Ffolliott, Peter F.; Gottfried, Gerald J.; Bennett, Duane A.; [and others], technical coordinators. Ecology and management of oak and associated woodlands: perspectives in the southwestern United States and northern Mexico: Proceedings; 1992 April 27-30; Sierra Vista, AZ. Gen. Tech. Rep. RM-218. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 195-198. 
67. Fechner, Gilbert H. 1985. Silvical characteristics of blue spruce. Gen. Tech. Rep. RM-117. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 19 p. 
68. Ffolliott, Peter F.; Gottfried, Gerald J. 1991. Natural tree regeneration after clearcutting in Arizona's ponderosa pine forests: two long-term case studies. Res. Note RM-507. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Moutnain Forest and Range Experiment Station. 6 p. 
69. Ffolliott, Peter F.; Thorud, David B. 1974. Vegetation for increased water yield in Arizona. Tech. Bull. 215. Tucson, AZ: University of Arizona, Agricultural Experiment Station. 38 p. 
70. Fitzhugh, E. Lee; Moir, William H.; Ludwig, John A.; Ronco, Frank, Jr. 1987. Forest habitat types in the Apache, Gila, and part of the Cibola National Forests, Arizona and New Mexico. Gen. Tech. Rep. RM-145. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 116 p. 
71. Floyd, Mary E. 1982. The interaction of pinon pine and gambel oak in plant succession near Dolores, Colorado. The Southwestern Naturalist. 27(2): 143-147. 
72. Floyd-Hanna, Lisa; DaVega, Anne; Hanna, David; Romme, William H. 1997. Chapin 5 fire vegetation monitoring and mitigation first year report. Unpublished report. Washington, DC: U.S. Department of the Interior, National Park Service, Mesa Verde National Park. 7 p. (+ Appendices). On file with: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory, Missoula, MT. 
73. Foxx, Teralene S.; Tierney, Gail D. 1987. Rooting patterns in the pinyon-juniper woodland. In: Everett, Richard L., compiler. Proceedings--pinyon-juniper conference; 1986 January 13-16; Reno, NV. Gen. Tech. Rep. INT-215. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 69-79. 
74. Freeman, C. E.; Dick-Peddie, W. A. 1970. Woody riparian vegetation in the Black and Sacramento Mountain ranges, southern New Mexico. The Southwestern Naturalist. 15(2): 145-164. 
75. Freeman, D. Carl; McArthur, E. Durant; Harper, K.T.; Blauer, A.C. 1981. Influence of environment on the floral sex ratio of monoecious plants. Evolution. 35(1): 194-197. 
76. Frischknecht, Neil C.; Plummer, A. Perry. 1955. A comparison of seeded grasses under grazing and protection on a mountain brush burn. Journal of Range Management. 8: 170-175. 
77. Fule, Peter Z.; Covington, W. Wallace; Moore, Margaret M. 1997. Determining reference conditions for ecosystem management of southwestern ponderosa pine forests. Ecological Applications. 7(3): 895-908. 
78. Ganey, Joseph L. 1999. Snag density and composition of snag populations on two National Forests in northern Arizona. Forest Ecology and Management. 117(1-3): 169-178. 
79. Ganey, Joseph L.; Block, William M.; Dwyer, Jill K.; [and others]. 1998. Dispersal movements and survival rates of juvenile Mexican spotted owls in northern Arizona. The Wilson Bulletin. 110(2): 206-217. 
80. Ganey, Joseph L.; Block, William M.; Dwyer, Jill K.; [and others]. 1998. Dispersal movements and survival rates of juvenile Mexican spotted owls in northern Arizona. The Wilson Bulletin. 110(2): 206-217. 
81. Ganey, Joseph L.; Block, William M.; Jenness, Jeffrey S.; Wilson, Randolph A. 1999. Mexican spotted owl home range and habitat use in pine--oak forest: implications for forest management. Forest Science. 45(1): 127-135. 
82. Ganey, Joseph L.; Duncan, Russell B.; Block, William M. 1992. Use of oak and associated woodlands by Mexican spotted owls in Arizona. In: Ffolliott, Peter F.; Gottfried, Gerald J.; Bennett, Duane A.; [and others], technical coordinators. Ecology and management of oak and associated woodlands: prespectives in the southwestern United States and northern Mexico: Proceedings; 1992 April 27-30; Sierra Vista, AZ. Gen. Tech. Rep. RM-218. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 125-128. 
83. 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. 
84. Gaylord, Eric S.; Preszler, Ralph W.; Boecklen, William J. 1996. Interactions between host plants, endophytic fungi, and a phytophagous insect in an oak (Quercus grisea X Q. gambelii) hybrid zone. Oecologia. 105(3): 336-342. 
85. Giesen, Kenneth M.; Braun, Clait E. 1993. Status and distribution of Columbian sharp-tailed grouse in Colorado. Prairie Naturalist. 25(3): 237-242. 
86. Gill, R. Bruce; Beck, Thomas D. I. 1990. Black bear management plan: 1990-1995. Division Report No. 15; DOW-R-D-15-90. Denver, CO: Department of Natural Resources, Colorado Division of Wildlife. 44 p. 
87. Gottfried, Gerald J.; DeBano, Leonard F. [n.d.]. Total shrub biomass of a New Mexico locust site in central Arizona. In: Proceedings, annual convention of the Society of American Foresters; [Date of conference unknown]; [Location of conference unknown]. [Place of publication unknown]. The Society of American Foresters: 310-314. 
88. Grover, B. L.; Richardson, E. A.; Southard, A. R. 1970. Quercus gambelii as an indicator of climatic means. Utah Academy of Science Proceedings. 47(Part I): 187-191. 
89. Hanks, Jess P.; Dick-Peddie, W. A. 1974. Vegetation patterns of the White Mountians, New Mexico. The Southwestern Naturalist. 18(4): 371-382. 
90. Hanks, Jess P.; Fitzhugh, E. Lee; Hanks, Sharon R. 1983. A habitat type classification system for ponderosa pine forests of northern Arizona. Gen. Tech Rep. RM-97. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 22 p. 
91. Harper, K. T.; Freeman, D. Carl; Ostler, W. Kent; Klikoff, Lionel G. 1978. The flora of Great Basin mountain ranges: diversity, sources, and dispersal ecology. In: Harper, Kimball T.; Reveal, F. L., eds. Intermountain biogeography: a symposium. The Great Basin Naturalist Memoirs No. 2. Provo, UT: Brigham Young University: 81-103. 
92. Harper, Kimball T.; Wagstaff, Fred J.; Kunzler, Lynn M. 1985. Biology management of the Gambel oak vegetative type: a literature review. Gen. Tech. Rep. INT-179. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 31 p. 
93. Harrington, H. D. 1964. Manual of the plants of Colorado. 2d ed. Chicago: The Swallow Press Inc. 666 p. 
94. Harrington, M. G. 1985. The effects of spring, summer, and fall burning on Gambel oak in a Southwestern ponderosa pine stand. Forest Science. 31(1): 156-163. 
95. Harrington, Michael G. 1987. Phytotoxic potential of Gambel oak on ponderosa pine seed germination and initial growth. Res. Paper RM-277. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 7 p. 
96. Hayward, C. Lynn. 1948. Biotic communities of the Wasatch Chaparral, Utah. Ecological Monographs. 18: 473-506. 
97. Heede, Burchard H. 1988. The influence of vegetation and its spacial distribution on sedement delivery from selected Arizona forests and woodlands. In: Erosion Control: Stay in Tune; 1988 February 25 - February 26; New Orleans, LA. Proceedings of Conference XIX. [Place of publication unknown]. International Erosion Control Association: 383-392. 
98. Heikes, Eugene. 1964. Tordon and other herbicides...field testing for the control of deep-rooted perennial weeds in Colorado. Down to Earth. 20: 9-12. 
99. Hess, Karl; Wasser, Clinton H. 1982. Grassland, shrubland, and forestland habitat types of the White River-Arapaho National Forest. Final Report. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 335 p. 
100. Hinckley, L. C. 1944. The vegetation of the Mount Livermore area in Texas. The American Midland Naturalist. 32: 236-250. 
101. Hodgson, Angela; Stacey, Peter. 1996. Dispersal and habitat use of Mexican spotted owls in New Mexico. Final report: Cooperative Agreement 28-C3-741. Reno, NV: University of Nevada - Reno, Department of Environmental Sciences. 85 p. 
102. Hoffman, Donald M. 1965. The scaled quail in Colorado: Range--population status--harvest. Tech. Publ. No. 18. Denver, CO: Colorado Department of Game, Fish, and Parks. 47 p. 
103. Hoffman, George R.; Alexander, Robert R. 1980. Forest vegetation of the Routt National Forest in northwestern Colorado: a habitat classification. Res. Pap. RM-221. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 41 p. 
104. Hutchings, Selar S.; Mason, Lamar R. 1970. Estimating yields of Gambel oak from foliage cover and basal area. Journal of Range Management. 23(6): 430-434. 
105. James, L. F.; Keeler, R. F.; Johnson, A. E.; [and others]. 1980. Plants poisonous to livestock in the western states. Agriculture Information Bulletin 415. Washington, DC: U.S. Department of Agriculture, Science and Education Administration. 90 p. 
106. Jefferies, Ned W. 1965. Herbage production on a Gambel oak range in southwestern Colorado. Journal of Range Management. 18(4): 212-213. 
107. Johnson, Kendall L. 1985. Volume and biomass on Gambel oak woodlands. In: Van Hooser, Dwane D.; Van Pelt, Nicholas, compilers. Growth and yield and other mensurational tricks: a regional technical conference. General Technical Report INT-193. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station: 82-85. 
108. Johnson, Paul S. 1993. Sources of oak reproduction. In: Loftis, David L.; McGee, Charles E., eds. Oak regeneration: Serious problems, practical recommendations: Symposium proceedings; 1992 September 8-10; Knoxville, TN. Gen. Tech. Rep. SE-84. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station: 112-131. 
109. Julander, Odell. 1937. Utilization of browse by wildlife. Transactions, 2nd North American Wildlife Conference. ?: 276-287. 
110. Julander, Odell; Robinette, W. Leslie. 1950. Deer and cattle range relationships on Oak Creek range in Utah. Journal of Forestry. 48(6): 410-415. 
111. Kartesz, John T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. Volume I--checklist. 2nd ed. Portland, OR: Timber Press. 622 p. 
112. Kaufmann, Merrill R.; Huckaby, Laurie S.; Regan, Claudia M.; Popp, John. 1998. Forest reference conditions for ecosystem management in the Sacramento Mountains, New Mexico. Gen. Tech. Rep. RMRS-GTR-19. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 87 p. 
113. Klemmedson, James O. 1987. Influence of oak in pine forests of central Arizona on selected nutrients of forest floor and soil. Soil Science Society of America Journal. 51(6): 1623-1628. 
114. Klemmedson, James O. 1991. Oak influence on nutrient availability in pine forests of central Arizona. Soil Science Society of America Journal. 55(1): 248-253. 
115. Knipe, Theodore. 1957. The javelina in Arizona: A research and management study. Wildlife Bulletin No. 2. Phoenix, AZ: State of Arizona, Game and Fish Department. 98 p. 
116. Kolb, T. E.; Stone, J. E. 2000. Differences in leaf gas exchange and water relations among species and tree sizes in an Arizona pine - oak forest. Tree Physiology. 20: 1-12. 
117. Komarkova, Vera; Alexander, Robert R.; Johnston, Barry C. 1988. Forest vegetation of the Gunnison and parts of the Uncompahgre National Forests: a preliminary habitat type classification. Gen. Tech. Rep. RM-163. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 65 p. 
118. Korstian, Clarence F. 1921. Effect of a late spring frost upon forest vegetation in the Wasatch Mountains of Utah. Ecology. 2(1): 47-52. 
119. Kruse, William H. 1992. Quantifying wildlife habitats within Gambel oak/forest/woodland vegetation associations in Arizona. In: Ffolliott, Peter F.; Gottfried, Gerald J.; Bennett, Duane A.; [and others], technical coordinators. Ecology and management of oak and associated woodlands: perspectives in the sw United States & n Mexico: Proceedings; 1992 April 27-30; Sierra Vista, AZ. Gen. Tech. Rep. RM-218. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 182-186. 
120. Kuchler, A. W. 1964. United States [Potential natural vegetation of the conterminous United States]. Special Publication No. 36. New York: American Geographical Society. 1:3,168,000; colored. 
121. Kufeld, Roland C. 1973. Foods eaten by the Rocky Mountain elk. Journal of Range Management. 26(2): 106-113. 
122. Kufeld, Roland C. 1983. Responses of elk, mule deer, cattle, and vegetation to burning, spraying and chaining of Gambel oak rangeland. Tech. Publ. 34. Fort Collins, CO: Colorado Division of Wildlife. 47 p. 
123. Kufeld, Roland C.; Stevens, Marilyn; Bowden, David C. 1981. Winter variation in nutrient and fiber content and in vitro digestibility of gambel oak [Quercus gambelii] and big sagebrush [Artemisia tridentata] from diversified sites in Colorado. Journal of Range Management. 34(2): 149-151. 
124. Kufeld, Roland C.; Wallmo, O. C.; Feddema, Charles. 1973. Foods of the Rocky Mountain mule deer. Res. Pap. RM-111. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 31 p. 
125. Kunzler, L. M.; Harper, K. T. 1980. Recovery of Gambel oak after fire in central Utah. The Great Basin Naturalist. 40(2): 127-130. 
126. Kunzler, L. M.; Harper, K. T.; Kunzler, D. B. 1981. Compositional similarity within the oakbrush type in central and northern Utah. The Great Basin Naturalist. 41(1): 147-153. 
127. Lanner, Ronald M. 1983. Trees of the Great Basin: A natural history. Reno, NV: University of Nevada Press. 215 p. 
128. Larsen, David R.; Johnson, Paul S. 1998. Linking the ecology of natural oak regeneration to silviculture. Forest Ecology and Management. 106(1): 1-7. 
129. Larson, Milo; Moir, W. H. 1987. Forest and woodland habitat types (plant associations) of northern New Mexico and northern Arizona. 2d ed. Albuquerque, NM: U.S. Department of Agriculture, Forest Service, Southwestern Region. 90 p. 
130. Lauver, Chrid L.; Jameson, Donald A.; Rittenhouse, Larry R. 1989. Management strategies for Gambel oak communities. Rangelands. 11(5): 213-216. 
131. Lefevre, R. E.; Klemmedson, J. O. 1980. Effect of Gambel oak on forest floor and soil of a ponderosa pine forest. Soil Science of America Journal. 44(4): 842-846. 
132. Loehle, Craig. 1988. Tree life history strategies: the role of defenses. Canadian Journal of Forest Research. 18(2): 209-222. 
133. Long, W. H. 1941. The durability of untreated oak posts in the Southwest. Journal of Forestry. 39: 701-704. 
134. Lull, Howard W.; Ellison, Lincoln. 1950. Precipitation in relation to altitude in central Utah. Ecology. 31(3): 479-484. 
135. Madany, Michael H.; West, Neil E. 1983. Livestock grazing-fire regime interactions within montane forests of Zion National Park, Utah. Ecology. 64(4): 661-667. 
136. Madany, Michael H.; West, Neil E. 1984. Vegetation of two relict mesas in Zion National Park. Journal of Range Management. 37(5): 456-461. 
137. Marquiss, R. W. 1969. Studies on Gambel's oak at the San Juan Basin Station. Progress Report PR 69-38. Fort Collins, CO: Colorado State University Experiment Station. 2 p. 
138. Marquiss, Robert W. 1972. Soil moisture, forage, and beef production benefits from gambel oak control in southwestern Colorado. Journal of Range Management. 25(2): 146-150. 
139. Marquiss, Robert W. 1973. Gambel oak control studies in southwestern Colorado. Journal of Range Management. 26(1): 57-58. 
140. Marti, Carl D. 1977. Avian use of an oakbrush community in northern Utah. The Southwestern Naturalist. 22(3): 367-374. 
141. Martin, Alexander C.; Zim, Herbert S.; Nelson, Arnold L. 1951. American wildlife and plants. New York: McGraw-Hill Book Company, Inc. 500 p. 
142. McCulloch, C. Y; Wallmo, O. C.; Ffolliott, P. F. 1965. Acorn yield of Gambel oak in northern Arizona. Res. Note RM-48. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 2 p. 
143. McKell, Cyrus M. 1950. A study of plant succession in the oak brush (Quercus gambelii) zone after fire. Salt Lake City, UT: University of Utah. 79 p. Thesis. 
144. Mitchell, Jerry M. 1984. Fire management action plan: Zion National Park, Utah. Record of Decision. 73 p. Report on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT. 
145. Moinat, A. D. 1956. Comparative yields of herbage from oak scrub and interspersed grassland in Colorado. Ecology. 37(4): 852-854. 
146. Moir, William H.; Ludwig, John A. 1979. A classification of spruce-fir and mixed conifer habitat types of Arizona and New Mexico. Res. Pap. RM-207. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 47 p. 
147. Mower, Kerry J.; Smith, H. Duane. 1989. Diet similarity between elk and deer in Utah. The Great Basin Naturalist. 49(4): 552-555. 
148. Mueggler, Walter F.; Campbell, Robert B., Jr. 1986. Aspen community types of Utah. Res. Pap. INT-362. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 69 p. 
149. Muldavin, Esteban H.; De Velice, Robert L.; Ronco, Frank, Jr. 1996. A classification of forest habitat types: Southern Arizona and portions of the Colorado Plateau. RM-GTR-287. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 130. 
150. Muller, Cornelius H. 1951. The significance of vegetative reproduction in Quercus. Madrono. 2: 129-137. 
151. Muzik, T. J. 1970. Weed biology and control. New York: McGraw-Hill Book Company, Inc. 273 p. 
152. Nastis, Anastasios S.; Malechek, John C. 1988. Estimating digestibility of oak browse diets for goats by in vitro techniques. Journal of Range Management. 41(3): 255-258. 
153. Neilson, R. P. 1981. Biogeography of Quercus gambelii and Quercus turbinella in relation to seedling drought response and atmospheric flow structure. Salt Lake City, UT: University of Utah. 135 p. Dissertation. 
154. Neilson, R. P.; Wullstein, L. H. 1980. Catkin freezing and acorn production in Gambel oak in Utah, 1978. American Journal of Botany. 67: 426-428. 
155. Neilson, R. P.; Wullstein, L. H. 1983. Biogeography of two southwest American oaks in relation to atmospheric dynamics. Journal of Biogeography. 10: 275-297. 
156. Neilson, Ronald P.; Wullstein, L. H. 1985. Comparative drought physiology and biogeography of Quercus gambelii and Quercus turbinella. The American Midland Naturalist. 114(2): 259-271. 
157. Neilson, Ronald P.; Wullstein, L. H. 1986. Microhabitat affinities of Gambel oak seedlings. The Great Basin Naturalist. 46(2): 294-298. 
158. Neuenschwander, L. F. [n.d.]. The fire induced autecology of selected shrubs of the cold desert and surrounding forests: A-state-of-the-art-review. Moscow, ID: University of Idaho, College of Forestry, Wildlife and Range Sciences. In cooperation with: Fire in Multiple Use Management, Research, Development, and Applications Program, Northern Forest Fire Laboratory, Missoula, MT. 30 p. Unpublished manuscript on file at: U.S. Department of Agriculture, Forest Service, Intermountain Fire Sciences Laboratory, Missoula, MT. 
159. Nixon, Elray S. 1967. A comparative study of the mountain brush vegetation in Utah. The Great Basin Naturalist. 27(2): 59-66. 
160. Ogle, Karen Ann. 1989. Influence of moisture content in Gambel oak leaves on Waterton Canyon fire behavior. Fort Collins, CO: Colorado State University. 63 p. Thesis. 
161. Ogle, Karen. 1988. Moisture content of Gambel oak leaves. Burning issues...for resource managers in the Rocky Mountain West. [Denver, CO: Colorado State Forest Service]. 2(3): 1-2. 
162. Patton, David R. 1975. Abert squirrel cover requirements in Southwestern ponderosa pine. Res. Pap. RM-145. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 12 p. 
163. Patton, David R.; Green, Win. 1970. Abert's squirrels prefer mature ponderosa pine. Res. Note RM-169. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 3 p. 
164. Pederson, Jordan C.; Farentinos, R.C.; Littlefield, Victoria M. 1987. Effects of logging on habitat quality and feeding patterns of Abert squirrels. The Great Basin Naturalist. 47(2): 252-258. 
165. Platt, Joseph B. 1976. Sharp-shinned hawk nesting and nest site selection in Utah. The Condor. 78(1): 102-103. 
166. Poreda, Stephen F.; Wullstein, Leroy H. 1994. Vegetation recovery following fire in an oakbrush vegetation mosaic. The Great Basin Naturalist. 54: 380-383. 
167. Rasmussen, D. Irvin. 1941. Biotic communities of Kaibab Plateau, Arizona. Ecological Monographs. 11(3): 229-275. 
168. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. 
169. Ream, Robert Ray. 1964. The vegetation of the Wasatch Mountains, Utah and Idaho. Madison, WI: University of Wisconsin. 178 p. Ph.D. thesis. 
170. Reynolds, Hudson G. 1962. Some characteristics and uses of Arizona's major plant communities. Journal of the Arizona Academy of Science. 2: 62-71. 
171. Reynolds, Hudson G.; Clary, Warren P.; Ffolliott, Peter F. 1970. Gambel oak for Southwestern wildlife. Journal of Forestry. 68(9): 545-547. 
172. Riggs, Robert A.; Urness, Philip J. 1989. Effects of goat browsing on Gambel oak communities in northern Utah. Journal of Range Management. 42(5): 354-360. 
173. Riggs, Robert A.; Urness, Philip J.; Gonzalez, Karen A. 1990. Effects of domestic goats on deer wintering in Utah oakbrush. Journal of Range Management. 43(3): 229-234. 
174. Risenhoover, Kenneth L.; Bailey, James A. 1985. Foraging ecology of mountain sheep: implications for habitat management. Journal of Range Management. 49(3): 797-804. 
175. Robinette, W. Leslie; Gashwiler, Jay S.; Morris, Owen W. 1959. Food habits of the cougar in Utah and Nevada. Journal of Wildlife Management. 23(3): 261-273. 
176. Rogers, Garry F. 1982. Then and now: a photographic history of vegetation change in the central Great Basin Desert. Salt Lake, UT: University of Utah Press. 152 p. 
177. Rominger, Eric M.; Dale, Alan R.; Bailey, James A. 1988. Shrubs in the summer diet of Rocky Mountain bighorn sheep. Journal of Wildlife Management. 52(1): 47-50. 
178. Sackett, Stephen S. 1980. Woody fuel particle size and specific gravity of southwestern tree species. Res. Note RM-389. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 4 p. 
179. Schier, George A. 1983. Vegetative regeneration of Gambel oak and chokecherry from excised rhizomes. Forest Science. 29(30): 499-502. 
180. Shiflet, Thomas N., ed. 1994. Rangeland cover types of the United States. Denver, CO: Society for Range Management. 152 p. 
181. Smith, Arthur D. 1950. Feeding deer on browse species during winter. Journal of Range Management. 3(2): 130-132. 
182. Smith, Arthur D. 1957. Nutritive value of some browse plants in winter. Journal of Range Management. 10: 162-164. 
183. Smith, Arthur D.; Hubbard, Richard L. 1954. Preference ratings for winter deer forages from northern Utah ranges based on browsing time and forage consumed. Journal of Range Management. 7: 262-265. 
184. Sopp, D. F.; Salac, S. S.; Sutton, R. K. 1977. Germination of Gambel oak seed. Tree Planter's Notes. 28(2): 4-5. 
185. Steinhoff, Harold W. 1979. Management of Gambel oak associations for wildlife and livestock. Denver, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Region. 119 p. Preliminary edition. 
186. Stephenson, Richard L. 1974. Seasonal food habits of Abert's squirrels, Sciurus aberti. Journal of the Arizona Academy of Sciences. 9:8. [Abstract]. 
187. Stevens, Richard; Davis, James N. 1985. Opportunities for improving forage production in the Gambel oak types of Utah. In: Johnson, Kendall L., ed. Proceedings, 3rd Utah shrub ecology workshop; 1983 August 30-31; Provo, UT. Logan, UT: Utah State University, College of Natural Resources: 37-41. 
188. 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. 10 p. 
189. Stoddart, L. A.; Holmgren, A. H.; Cook, C. W. 1949. Important poisonous plants of Utah. Special Report No. 2. Logan, UT: Utah State Agricultural College, Agricultural Experiment Station. 21 p. 
190. Stricklan, Dave; Flinders, Jerran T.; Cates, Rex G. 1995. Factors affecting selection of winter food and roosting resources by porcupines in Utah. The Great Basin Naturalist. 55(1): 29-36. 
191. Stuever, Mary C.; Hayden, John S. 1996. Plant associations (habitat types) of the forests and woodlands of Arizona and New Mexico. Final report submitted to: U.S. Department of Agriculture, Forest Service, Southwestern Region. Contract R3-95-27. Placitas, NM: Seldom Seen Expeditions, Inc. 520 p. 
192. Sweeney, John R.; Sweeney, James M.; Steinhoff, Harold W. 1979. Effects of snow on browse production by Gambel oak. In: Swanson, Gustav A., technical coordinator. The mitigation symposium: a national workshop on mitigating losses of fish and wildlife habitats; 1979 July 16-20; Fort Collins, CO. General Technical Report RM-65. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station: 637-638. 
193. Szaro, Robert C.; Balda, Russell P. 1979. Effects of harvesting ponderosa pine on nongame bird populations. Res. Pap. RM-212. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 8 p. 
194. Szaro, Robert C.; Balda, Russell P. 1982. Selection and monitoring of avian indicator species: an example from a ponderosa pine forest in the Southwest. Gen. Tech. Rep. RM-89. Fort Collins, CO: U.S. Department of Agriculture, ForestService, Rocky Mountain Forest and Range Experiment Station. 8 p. 
195. Tew, Ronald K. 1966. Soil moisture depletion by Gambel oak in northern Utah. Res. Note INT-54. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 7 p. 
196. Tew, Ronald K. 1967. Soil moisture depletion by Gambel oak in central Utah. Res. Note INT-74. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 8 p. 
197. Tew, Ronald K. 1969. Converting Gambel oak sites to grass reduces soil-moisture depletion. Res. Note INT-104. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 4 p. 
198. Tiedemann, A. R.; Clary, W. P.; Barbour, R. J. 1987. Underground systems of Gambel oak (Quercus gambelii) in central Utah. American Journal of Botany. 74(7): 1065-1071. 
199. Tiedemann, Arthur R.; Clary, Warren P. 1985. Nitrogen distribution in northcentral Utah Gambel oak stands. In: Johnson, Kendall L., ed. Proceedings, 3rd Utah shrub ecology workshop; 1983 August 30-31; Provo, UT. Logan, UT: Utah State University, College of Natural Resources: 13-18. 
200. Tucker, J. M.; Neilson, R. P.; Wullstein, L. H. 1980. Hermaphroditic flowering in Gambel oak. American Journal of Botany. 67: 1265-1267. 
201. Tucker, John M. 1961. Studies in the Quercus undulata complex. I. A preliminary statement. American Journal of Botany. 48(3): 202-208. 
202. U.S. Department of Agriculture, Agricultural Research Service. 1968. 22 plants poisonous to livestock in the Western states. Agriculture Information Bulletin No. 327. Washington, DC: U.S. Department of Agriculture, Agricultural Research Service, Animal Disease and Parasite Research Division & Crops Reserch Div. 64 p. 
203. U.S. Department of Agriculture, Soil Conservation Service. 1994. Plants of the U.S.--alphabetical listing. Washington, DC: U.S. Department of Agriculture, Soil Conservation Service. 954 p. 
204. Vallentine, John F.; Schwendiman, Dewayne. 1973. Spot treatment for Gambel oak control. Journal of Range Management. 26(5): 382-383. 
205. Van Epps, Gordon A. 1974. Control of Gambel oak with three herbicides. Journal of Range Management. 27(4): 297-301. 
206. Wagstaff, Fred J. 1984. Economic considerations in use and management of Gambel oak for fuelwood. Gen. Tech. Rep. INT-165. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 8 p. 
207. Wagstaff, Fred J. 1985. Economics of using Gambel oak for firewood. In: Johnson, Kendall L., ed. Proceedings, 3rd Utah shrub ecology workshop; 1983 August 30-31; Provo, UT. Logan, UT: Utah State University, College of Natural Resources: 53-58. 
208. Welch, Bruce L. 1981. Nutritive value of big sagebrush and other shrubs. In: Proceedings--shrub establishment on disturbed arid and semi-arid lands symposium; 1980 December 2-3; Laramie, WY. Laramie, WY: Wyoming Game and Fish Department: 9-22. 
209. Welch, Bruce L. 1989. Nutritive value of shrubs. In: McKell, Cyrus M., ed. The biology and utilization of shrubs. San Diego, CA: Academic Press, Inc: 405-424. 
210. Welsh, Stanley L.; Atwood, N. Duane; Goodrich, Sherel; Higgins, Larry C., eds. 1987. A Utah flora. The Great Basin Naturalist Memoir No. 9. Provo, UT: Brigham Young University. 894 p. 
211. West, Neil E.; Tausch, Robin J.; Tueller, Paul T. 1998. A management-oriented classification of pinyon-juniper woodlands of the Great Basin. Gen. Tech. Rep. RMRS-GTR-12. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 42 p. 
212. Wilcox, Richard B.; Brotherson, Jack D.; Evenson, William E. 1981. Canopy influence on understory community composition. Northwest Science. 55(3): 194-201. 
213. Williams, Stephen E.; Aldon, Earl F. 1976. Endomycorrhizal (vesicular arbuscular) associations of some arid zone shrubs. The Southwestern Naturalist. 20(4): 437-444. 
214. Winward, A. H. 1985. Perspectives on Gambel oak management on national forests of the Intermountain region. In: Johnson, Kendall L., ed. Proceedings, 3rd Utah shrub ecology workshop; 1983 August 30-31; Provo, UT. Logan, UT: Utah State University, College of Natural Resources: 33-35. 
215. Wirsing, John M.; Alexander, Robert R. 1975. Forest habitat types on the Medicine Bow National Forest, southeastern Wyoming: preliminary report. Gen. Tech. Rep. RM-12. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 11 p. 
216. Woyda, Ann L.; Kessler, Winifred B. 1982. The response of selected owl species to silvicultural treatments on the Dixie National Forest, Utah. Final Report on Cooperative Agreement No. INT-81-129-CA. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 46 p. 
217. Wright, Henry A. 1972. Shrub response to fire. In: McKell, Cyrus M.; Blaisdell, James P.; Goodin, Joe R., eds. Wildland shrubs--their biology and utilization: Proceedings of a symposium; 1971 July; Logan, UT. Gen. Tech. Rep. INT-1. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station: 204-217. 
218. Wright, Henry A.; Neuenschwander, Leon F.; Britton, Carlton M. 1979. The role and use of fire in sagebrush-grass and pinyon-juniper plant communities: A state-of-the-art review. Gen. Tech. Rep. INT-58. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 48 p. 
219. Wullstein, L. H.; Neilson, R. P. 1985. Seedling survival and biogeography of Gamebel oak (Quercus gambelii) in northern Utah. In: Johnson, Kendall L., ed. Proceedings, 3rd Utah shrub ecology workshop; 1983 August 30-31; Provo, UT. Logan, UT: Utah State University, College of Natural Resources: 1-3. 
220. Youngblood, Andrew P.; Mauk, Ronald L. 1985. Coniferous forest habitat types of central and southern Utah. Gen. Tech. Rep. INT-187. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 89 p. 
221. Harrington, M. G. 1982. Stand, fuel, and potential fire behavior characteristics in an irregular southeastern Arizona ponderosa pine stand. Res. Note RM-418. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Forest and Range Experiment Station. 6 p.