This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. Diseases and Environmental Factors of the Pinyon-Juniper Communities D. J. Weber E. D. Bunderson J. N. Davis D. L. Nelson A. Hreha Abstract-The pinyon-juniper woodland is the dominant ecosystem in Utah. While it is a very successful ec()system, it is not without its disease problems. The limiting soil nutrients appear to be nitrogen, phosphorous, and potassium. Temperature and moisture gradients are limiting factors in the growth of pinyon and juniper. Juniper decline appears to be related to drought and temperature stress and increased salts. A number of pathogens occur on Pinus edulis and Juniperus osteosperma. The most frequent pathogens on junipers are the rust fungi. Mistletoe was more common on pinyon than juniper but mistletoe infection has an impact on both. The pinyon-juniper woodland is a widespread vegetation type in the Southwestern United States that is estimated to cover from 40 to 50 million hectares (Allred 1964; Tausch and Tueller 1990). The pinyon-juniper vegetation provides a source of fuel, building materials, charcoal, pine nuts, Christmas trees, and folk medicines (Cronquist and others 1972; Gallegos 1977; Hurst 1977; Lanner 1975; Tueller and others 1979). About 80 percent of the acreage is grazed by livestock and wildlife (Bunderson and others 1986b; Clary 1975). In Utah, this ecosystem is a large component (62,705 km 2 or 28.6 percent) of the vegetation (Kuchler 1964). The pinyon-juniper woodlands are valued for their watershed, aesthetic, and recreational values (Gifford and Busby 1975). The pinyon-juniper woodlands also have a range of diseases. They range from non-pa thogen types (environmental factors) to specific pathogens. Both types will be discussed in this paper. The purpose of this manuscript is to review the non-pathogenic factors and pathogens present in pinyon-juniper woodlands. In: Monsen, Stephen B.; Stevens, Richard, comps. 1999. Proceedings: ecology and management of pinyon-juniper communities within the Interior West; 1997 Septeinber 15-18; Provo, UT. Proc. RMRS-P-9. Ogden, UT: U.s. Department of Agriculture, Forest Service, Rocky Mountain Research Station. D. J. Weber is with the Department of Botany and Range Science and E. D. Bunderson (deceased) was with the Department of Instructional Science, Brigham Young University, Provo, UT 84602. J. N. Davis and D. L. Nelson are with the USDA Forest Service, Rocky Mountain Research Station, Shrub Sciences Laboratory, Provo, UT 84606. A. Hreha is with the Red Butte Botanical Garden, University of Utah, Salt Lake City, UT 84112. 118 Influence of Environmental Factors ____________ Soil and Mineral Factors Soil samples and foliage samples (255 trees) were collected from 17 pinyon-juniper sites throughout Utah (fig. 1, table 1). Mineral analysis of soils and leaf samples were determined. The mineral concentration was correlated with the mineral concentrations of the leaves at the different sites. Statistical and factorial analyses suggested that the primary limiting soil nutrients in the native soils were nitrogen, phosphorous, and potassium. The linear correlation coefficient of foliage mineral composition and soil mineral composition was 0.66 for nitrogen and potassium and 0.49 for sodium and phosphorous. Rotated orthogonal Figure 1-Location of the 17 pinyon-juniper study sites in Utah. USDA Forest Service Proceedings RMRS-P-9. 1999 Table 1-Specific names of the 17 primary pinyon-juniper study sites in Utah. Number 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 Site name Jackson Springs Tobin Bench Peters Point Alkali Ridge Cyclone Flat Indian Peak Ephraim Manti Black Mountain Triangle Mountain Beaver Ridge Gordon Creek Dutch John Taylor Flat Rabbit Gulch Henry Mt (Stevens Narrows) Henry Mt (Airplane Flat) Utah, Wyoming, and Washington. The reported pathogens on Pinus edulis were: Acanthophysium albida (Gilbertson and others 1974) Armillaria mellea (Plant Disease Index 1960) Arceuthobium campylopodum (Peterson 1961) Arceuthobium divaricatum (Hreha and Weber 1979) Coleosporium crowellii (Christenson and Peterson 1961) Coleosporium jonesii (Gilbertson and McHenry 1969) Coleosporium ribicola (Peterson 1962) Cronartium occidentale (Plant Disease Index 1960) Dacryobolus karstenii (Gilbertson and others 1975) Heterobasidion annosum (Tegethoff 1973) Leptographium wageneri (Landis and Helburg 1976) Phellinus pini (Plant Disease Index 1960) Phoradendronjuniperinum (Hreha and Weber 1979) Tomentella chlorina (Gilbertson and others 1974) Verticicladiella sp. (Wagener and Mielke 1961) Verticicladiella wagenerii (Walters and Walters 1977) Diseases Reported for Junipers factors from varimax factor analysis were 0.79 for nitrogen, 0.73 for phosphorous and 0.50 for potassium. Correlation of factors greater than an absolute value of 0.25 are significant (Bunderson and others 1986a). Increased concentration of sodium resulted in decreased growth of junipers which would indicate that J. osteosperma is a salt-sensitive species. Temperature and moisture gradients were also distinct growth limiting factors in this ecosystem (Bunderson and others 1985). Juniper Decline, a Non-Pathogenic Disease Juniper decline is common in southwestern Utah. The characteristic symptom is for the distal foliage to become chlorotic and die. Mortality progresses along twigs until whole branches or the entire tFee dies. While juniper decline was observed in Natural Bridges National Monument and Needles area of Canyon land National Park, no pathogenic agent appeared to be responsible for the decline problem. There did not appear to be any high correlation between high or low amounts of minerals in the soil. It is suggested that the juniper decline is a combination of drought and temperature stress which reduces the water resources. The increased uptake of salts result in complexing of the iron, magnesium and calcium to form complex crystals in the leaves which are characteristic of the decline symptoms (Weber and others 1995). Diseases Caused by Organisms __________ Diseases Reported for Pinyon Pine The printed literature was searched by computer and manual searches of several western disease herbariums were done. The States covered by the herbarium searches were Arizona, Colorado, Idaho, Nevada, New Mexico, Oregon, USDA Forest Service Proceedings RMRS-P-9. 1999 The reported pathogens on Juniperus osteosperma (Utah Juniper) were: Antrodia ferox (Hawksworth 1950) Daedaleajuniperina (Gilbertson 1975) Diplomitoporus rimosus (Hedgecock 1912) Fomesjuniperinus (Bethel 1918) Gymnosporangium harknessianum (Plant Disease Index 1960) Gymnosporangium inconspicuum (Bethel 1918) Gymnosporangiumjuvenescens (Goodding 1919) Gymnosporangium kernianum (Bethel 1918) Gymnosporangium multiporum (Bethel 1918) Gymnosporangium nelsonii (Bailey 1970) Gymnosporangium speciosum (Bethel 1918) Poria rimosa (Gill 1941) Pyrofomes (Fomes) demidoffii (Gilbertson 1974) Trametes sepium (Hawksworth 1950) Uredo phoradendri (Hawksworth 1952) Correlation of Diseases and Environment Pathogens and Physiological Diseases The diseases present on J. osteosperma was determined on 17 sites in Utah (fig. 1). The most frequent pathogen on the research sites was Gymnosporangium (rust fungi). Gymnosporangium inconspicuum was the most common rust fungus followed in frequency and severity by G. nelsonii, G. kernianum and G. speciosum. Mold-mildew type of diseases were correlated with high summer temperature and fall precipitation. Wood rot was common and correlated with low winter temperatures and low soil nitrate. Needle blight, shoot dieback, and needle cast symptoms were common and considered abiotic in origin. Needle blight was correlated with higher soil salinity. Mistletoe, Phoradendron juniperinum was present in seven sites (Bunderson and others 1986b). 119 Table 2-Percent infection comparing pinyon and juniper on rim, forest, and burned areas of the south rim of the Grand Canyon. Pinyon Juniper Rim Forest 32.3 46.8 30.6 31.8 Burned 0.02 0.02 Mistletoe on Pinyon and Juniper The distribution and effects of mistletoes on the pinyonjuniper vegetation along the south rim ofthe Grand Canyon was determined (Hreha and Weber 1979). Arceuthobium diuaricatum, which infects Pinus edulis, is spread by a forced ejection mechanism of the mistletoe. Juniperus osteosperma is infected by Phoradendronjuniperinum, which is spread by birds. Fire was the most effective factor in limiting the spread of the mistletoes. The trees that had regrown in the burned areas were the only areas devoid of mistletoe infection (table 2). The incident of infection increases as trunk diameter and height increases in both pinyon and juniper (Hreha and Weber 1979). While in some cases, the non-pathogenic factors and the pathogens cause death of the trees, no control measures are used. On the other hand, the replacement seedlings appear to be more than adequate to replace lost trees. 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