1Up Info - A Portal with a Difference

1Up Travel - A Travel Portal with a Difference.    
1Up Info
   

Earth & EnvironmentHistoryLiterature & ArtsHealth & MedicinePeoplePlacesPlants & Animals  • Philosophy & Religion  • Science & TechnologySocial Science & LawSports & Everyday Life Wildlife, Animals, & PlantsCountry Study Encyclopedia A -Z
North America Gazetteer


You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Tree > Species: Juniperus monosperma | Oneseed Juniper
 

Wildlife, Animals, and Plants

 


Wildlife, Animals, and Plants

 

Wildlife Species

  Amphibians

  Birds

  Mammals

  Reptiles

 

Kuchler

 

Plants

  Bryophyte

  Cactus

  Fern or Fern Ally

  Forb

  Graminoid

  Lichen

  Shrub

  Tree

  Vine


VALUE AND USE

SPECIES: Juniperus monosperma | Oneseed Juniper
WOOD PRODUCTS VALUE : The relatively small stature and multiple stems of oneseed juniper limit its usefulness as a timber species. The wood currently has little commercial value but was formerly used locally for fenceposts, poles, railroad ties, and mine timbers [16]. Oneseed juniper wood is described as strong and long-grained [28]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : Pinyon-juniper woodlands provide good habitat for mule deer, bighorn sheep, bison, wild horses, pronghorns, coyotes, bobcats, badgers, porcupines, rabbits, mice, voles, woodrats, squirrels, and numerous birds [16]. The foliage and berries of oneseed juniper provide food for many species of birds and mammals. Browse: The foliage of oneseed juniper appears to be of little value to domestic livestock. Sheep and goats may browse this species to a limited degree in some areas [13,35]. Oneseed juniper browse may induce abortions in domestic livestock under certain circumstances [73]. Deer utilize the foliage to at least a limited extent [13,35,52]. Mahgoub and others [51] observed fairly heavy utilization in parts of south-central New Mexico where juniper can represent up to 20 percent of the annual diet of mule deer. Oneseed juniper foliage is reported to be a major mule deer food item from January through March in parts of southeastern New Mexico [63]. Pronghorns also browse oneseed juniper, and in some areas, winter use may be fairly heavy [10,74]. Bighorn sheep and elk consume at least small amounts of juniper browse in certain locations [63]. Fruit: The berrylike fruits of oneseed juniper serve as an abundant and readily available food source for a wide range of wildlife species. The bright berries tend to remain on the tree and can provide food year-round [16]. Fruits are initially plump and juicy but become dry and leathery by the second winter [65]. Berry ripening usually corresponds with the arrival of winter residents to the pinyon-juniper woodlands [64]. Oneseed juniper berries represent an extremely important food source to a number of bird species. Berries are abundant, easily acessible, and nutritious [64]. It is estimated that avian population densities may be 70 percent greater during years with abundant juniper berry crops (generally every 2 to 5 years) [5]. Studies with captive birds have revealed that an average Townsend's solitaire can consume approximately 240 berries per day, or 36,000 to 84,000 per winter [5,64]. In some areas at least 97 percent of the Townsend's solitaire's winter diet may be made up of oneseed juniper berries [65]. Robins also consume large numbers of juniper berries. An individual bird can eat 220 berries per day or 33,000 per winter [5]. Balda [5] reported 20,000 berries per cubic meter of juniper foliage in 1973, but by September 1974, birds and other dispersal agents had reduced berry numbers to 300 per cubic meter. Birds and mammals serve as important dispersal agents for seeds of oneseed juniper. Many bird species disperse seed up to 6.3 miles (10 m) or more from the seed source [5]. Sheep and domestic cattle can also facilitate the dispersal of oneseed juniper [40]. A number of the following species known to consume oneseed juniper are important dispersal agents [64]: food source probable role northern flicker berry disperser Steller's jay berry disperser mountain chickadee flesh --- plain titmouse flesh --- sage thrasher berry disperser American robin berry disperser Townsend's solitaire berry disperser western bluebird berry disperser evening grosbeak seed probable Cassin's finch seed probable desert cottontail berry disperser black-tailed jackrabbit berry disperser cliff chipmunk seed probable rock squirrel seed probable golden mantled ground squirrel seed probable deer mice seed probable Mexican woodrat seed probable coyote berry disperser gray fox berry disperser Other wildlife species known to consume oneseed juniper berries include: mule deer, western chipmunk, antelope ground squirrel, squirrels, bear, javelina, pocket mouse, rabbits, and raccoon [40,63,72,73]. PALATABILITY : The fruits of oneseed juniper are sweet tasting and highly palatable to many birds and mammals [64]. They appear to remain palatable even when dry. The foliage is relatively unpalatable to most species, although it is reported to be somewhat more palatable than most other junipers [13]. The palatability of oneseed juniper to livestock and wildlife species in two western states has been rated as follows [14]: CO UT Cattle poor poor Sheep poor fair Horses poor poor Pronghorn ---- fair Elk ---- fair Mule deer ---- fair Small mammals ---- good Small nongame birds ---- good Upland game birds ---- good Waterfowl ---- poor NUTRITIONAL VALUE : Oneseed juniper is rated as poor in overall protein and energy value [14]. However, many species of birds apparently obtain at least moderate energy value from the berries [5]. These fruits provide a comparatively rich source of carbohydrates for a number of birds [64]. Caloric value of oneseed juniper berries is as follows [64]: size mg/unit cal/mg cal/unit berries 6.6 mm diameter 107.49 4.57 490.82 seeds 4.9 x 3.6 mm 37.52 4.66 174.85 flesh --- 69.97 4.52 315.97 COVER VALUE : Oneseed juniper provides good cover for a number of birds and mammals including quail, wild turkeys, deer, and songbirds [63]. The degree to which oneseed juniper provides environmental protection during one or more seasons for wildlife species is as follows [14]: CO UT Pronghorn ---- good Elk ---- good Mule deer fair good White-tailed deer fair ---- Small mammals good good Small nongame birds good good Upland game birds ---- good Waterfowl ---- poor VALUE FOR REHABILITATION OF DISTURBED SITES : Oneseed juniper is rated as having low overall value for short-term rehabilitation but high value for long-term rehabilitation [14]. It has not been widely used in the past for rehabilitation projects due to unreliable seed germination caused by inhibitors in the seed coat and dormancy [21]. Fertilizers, wood chip or straw mulch, plastic mesh for protection against rodents, and drip irrigation can all contribute to increased survival on disturbed sites [20,21]. Oneseed juniper has been successfully planted on a number of surface coal and uranium mines in the Southwest [20]. Improved techniques have resulted in survival rates of 70 percent to 99 percent [20,21]. On certain New Mexico sites, drip irrigation is somewhat more effective than mulch, while triple-superphosphate aids growth more than slow-release fertilizers [20]. Seed germination can be enhanced by leaching seeds with water at 68 to 75 degrees Fahrenheit (20-24 deg C) and cold stratification for 90 days, or seeds should be treated with water and GA3 or ethephon only, applied 30 days prior to cold stratification [21]. Planting dates can significantly influence seedling survival. On the New Mexico test sites, July planting dates produced best results at higher elevations, whereas August plantings were most successful on low-elevation sites [20]. Seedling survival at several New Mexico sites was as follows [20,21]: Raton, NM Site Grants, NM Site planting % survival treatment % survival July 73 mulched 96 May 55 non-mulched 89 August 48 treatment % survival May-fertilized 22 May-unfertilized 88 July-fertilized 62 July-unfertilized 86 August-fertilized 3 August-unfertilized 95 Coal mine site planting % survival 2 years after planting August 47 September 16 November 14 Transplanting containerized seedlings onto disturbed sites has also been successful [20,21]. Survival of transplants is apparently dependent on moisture availability [21]. In New Mexico, survival is best when trees are planted after the June drought but before the ground freezes [20,21]. Mulch which aids in water conservation can enhance survival on dry sites, and on extremely arid sites, drip irrigation may be necessary [20,21]. Fertilizer may improve survival on some sites particularly when combined with irrigation [20]. Applications of fertilizer should be made near the base of the tree but not in the same hole in which the tree was planted [20]. OTHER USES AND VALUES : Native American peoples historically used oneseed juniper for a variety of purposes. Wood was used for bows and arrows by the Kiowa, Commanche, Cheyenne, and Apache [28]. A number of North American peoples ate the fruit or ground them into flour for bread [73]. Prayer sticks were made from wood, and a green dye, fibrous mats, and saddles were fashioned from the bark [73]. Parts of the tree were also used as building materials and for medicinal purposes [40]. During historic times, oneseed juniper was used as a fuel source, as fenceposts, charcoal, mine timbers, posts, cellulose, and in a number of chemical products [40]. Springfield [71] noted that many species of juniper may have potential value for the production of charcoal, pulp, particleboard, chip products, fiber, or in certain chemicals. Oneseed juniper was first cultivated in 1900 [42]. MANAGEMENT CONSIDERATIONS : Pinyon-juniper woodlands have been increasing in extent since settlement times. In many parts of Southwest, oneseed juniper and other species have encroached into adjacent grasslands [35,56,80]. A decrease in fire frequency has often been cited as the probable cause of this increase [79], but overgrazing offers another possible explanation. Past management efforts have largely focused on halting the juniper invasion through mechanical or chemical means. Little regard was given to possible wildlife use of these areas, or to potential wood products value of these species. These factors should be considered when attempting to devise and implement management strategies in pinyon-juniper woodlands. Strategies aimed at preserving wildlife habitat while allowing carefully managed grazing opportunities should be favored. In many cases juniper removal alone does little to increase long-term forage potential. Mechanical control: A number of methods of mechanical removal have been used with varying success. Cabling, chaining, bulldozing, and various means of hand removal have been used in attempts to convert these woodlands to grasslands. Generally, cabling or chaining is most effective on even-terrain sites with approximately 250 trees per acre or less, and with at least half of those trees greater than 10 feet (3.1 m) [4,41,71]. Neither the single chaining nor double chaining method effectively kills trees less than 10 feet (3.1 m) in height [71]. In many areas, junipers and pinyons start to resume dominance as soon as 28 years after cabling [69]. Oneseed juniper seeds remain viable buried in the soil on-site or are dispersed from off-site by birds and mammals [69]. In many areas, particularly with many young tree prior to treatment, reinvasion is rapid, and results do not appear to justify these relatively expensive attempts at control [61]. Junipers may become dominant particularly rapidly on sites with deeper soils [68]. Poor results have also been obtained on rocky soils, which seldom produce good graminoid cover after juniper removal [67]. Stands should have few young trees and at least 15 percent residual grass cover for these mechanical treatments to be effective in promoting increases in forage [67]. Some researchers recommend using fire or herbicides as a second treatment approximately 5 years after cabling to increase tree kill [67]. Bulldozing is most effective on sites with small- to medium-sized trees and tree densities of 100 to 150 per acre [41,71]. Severson [70] reported poor results after pinyon-juniper woodlands in New Mexico were thinned and bulldozed. Differences in densities between most treated and untreated areas were not detectable 13 to 18 years later [70]. No significant differences were observed between bulldozed and untreated/thinned treatments [70]. Crushing even-aged mature stands and hand removal of individual trees have been tested, although both methods are expensive and have somewhat limited utility [3,41]. Mechanical removal of oneseed juniper has not produced increased water yields in experiments [19]. Chemical control: The foliage of junipers tends to be resistant to herbicides, and leaves have little surface area for absorption [41]. Junipers can reportedly be killed by chemicals such as arsenite, ammonium sulfate, esters of 2,4-D, and 2,4,5-T, polychlorobenzoic acid, and picloram. See Springfield [71] and Johnsen [41] for details. Range condition: Many pinyon-juniper ranges are now in relatively poor condition. The following species are indicative of range condition on certain Arizona oneseed juniper sites [32,33]: excellent: black gama (Bouteloua eriopoda), Indian ricegrass (Oryzopsis hymenoides), blue grama (B. gracilis), winterfat (Eurotia lanata), cliffrose (Cowania spp.), and fourwing saltbush (Atriplex canescens). good: Indian ricegrass, black grama, blue grama, needlegrass (Stipa spp.), and spike muhly (Muhlenbergia wrightii). fair: blue grama, bare soil. poor: broom snakeweed (Gutierrezia sarothrae), ringgrass (Muhlenbergia torreyi), often much erosion. Production: Herbage production values are variable in pinyon-juniper woodlands. Springfield [71] reported an inverse relationship between tree canopy and average herbage production as follows: tree canopy average herbage production 0% 600 lbs per acre 20% 300 lbs per acre 80% 50 lbs per acre Several studies have examined the influence of oneseed juniper canopy on understory vegetation. Results suggest fairly distinct vegetative zones surrounding oneseed junipers. Relatively little vegetation grows closest to the tree where litter accumulation is greatest and shading most extreme [1,66]. Generally such species as blue grama, sand muhly (Muhlenbergia arenicoloides), skunkbush sumac (Rhus trilobata), and algerita (Berberis trifoliata) occur here [1]. The second zone, which extends outward beneath the canopy, is represented by creeping muhly (Muhlenberiga repens), broom snakeweed, galleta (Hilaria jamesii), sideoats grama (Bouteloua curtipendula), blue grama , and western wheatgrass (Pascopyrum smithii) [1]. Production here was found to be approximately 293 pounds air-dry herbage per acre [2]. Blue grama, galleta , wolftail (Lycurus phleoides), mat muhly (Muhlenbergia richardsonis), scarlet globemallow (Sphaeralcea coccinea), dropseed (Aristida spp.), and hairy grama (Bouteloua hirsuta) are often most prevalent in the outer zone or in tree interspaces [1]. In some areas, western wheatgrass and broom snakeweed are well represented in interspaces which receive full sunlight [2]. Generally, cool-season grasses such as prairie junegrass (Koeleria cristata), western wheatgrass, bottlebrush squirreltail (Sitanion hystrix), and mutton bluegrass (Poa fendleriana) occur more abundantly under the canopy of oneseed juniper than in the interspaces [1,17]. Schott and Pieper [66] reported that oneseed juniper canopy crown diameter is negatively correlated with the basal area of grasses. Such factors as shading, decreased soil moisture due to absorption by oneseed juniper roots, and possible chemical properties of oneseed juniper litter, all effect the composition of understory vegetation [2,38,66]. Fertilization: The diameter of oneseed juniper was found to be largely unaffected by the addition of nitrogen fertilizer in a New Mexico study, although the growth of lateral branches and the apex was enhanced [63].

Related categories for Species: Juniperus monosperma | Oneseed Juniper

Send this page to a friend
Print this Page

Content on this web site is provided for informational purposes only. We accept no responsibility for any loss, injury or inconvenience sustained by any person resulting from information published on this site. We encourage you to verify any critical information with the relevant authorities.

Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

About Us | Contact Us | Terms of Use | Privacy | Links Directory
Link to 1Up Info | Add 1Up Info Search to your site

1Up Info All Rights reserved. Site best viewed in 800 x 600 resolution.