Knowledge (XXG)

Ponderosa pine forest

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they tend to burn more severely. They often kill large continuous expanses of vegetation, consume the forest floor, volatilize nutrients, provide for exotic species introductions, increase soil erosion, and, in general, create forest conditions that may not be favorable to society. The long-term consequences are not well understood for issues such as water quality and wildlife habitat. Nor will the sense of place that forests often provide which, in some cases, will not be replaced for many generations.
688: 93: 31: 175: 343: 20: 414:) rapidly regenerates after fire and captures and recycles nitrogen. Because of the range of species that can occur with ponderosa pine and their wide range of tolerance (e.g., shade, competition, fire) along with how they interact with disturbances a plethora of vegetative compositions and structures can occur within ponderosa pine forests arranged and interspersed in a variety of 737:
on the ponderosa pine PVT, grass cover tended to decrease ponderosa pine seedling establishment and survival. However, when heavy livestock grazing ceased in the early 1900s in the southwestern United States, dense stands of ponderosa pine seedlings became established. Because of fire exclusion, climate changes, and other factors these trees readily developed into dense stands.
158:, it can be 240 days. Annual precipitation is about 15 to 20 inches (380 to 510 mm) in the more pure pine areas, but where there are combinations of pine and other conifers at moderate elevations, the precipitation can total 30 inches (760 mm). In the far western sector, only 25 percent of this moisture falls in the warmest months. In the 1010: 905: 854: 711:
Ponderosa pine forests appear to have evolved with fire and many authors have suggested that their composition and structure are dependent on the vegetation's relations with fire. However, when wildfires burn altered ponderosa pine forests, the extent or area burned is similar to historical times but
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Ponderosa pine forest is the largest western forest type in the United States. Ponderosa pine is the principal species on over 110,000 km (27,000,000 acres) and is present on an additional 55,000 km (14,000,000 acres). Within the western United States, California alone contains the greatest
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and harvesting of ponderosa pine forests was occurring by the mid-1800s. Ponderosa pine was extensively harvested, altering both forest composition and structure. In mesic forests, grand fir and/or white fir and Douglas-fir rapidly colonized these sites when ponderosa pine was harvested. Especially
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spp.), or too old to resist attack. Pine engraver and fir engraver beetles attacked young, densely stocked ponderosa pine or removed trees scorched by low-intensity surface fires and/or trees severely infected with disease. Sometimes disease and insect infestations increased during droughts when
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by Native Americans augmented and even dominated burning in several locations. In the northern Rocky Mountains of Idaho and western Montana, dry settings of ponderosa pine forests historically burned by low severity surface fires that did not kill overstory trees at 15 to 23 year mean return
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origin. The physical properties of the soil, and thus its moisture-retaining capacity, play an important role in the tree's development, possibly more than the chemistry of the soil. Studies have shown strong relationships between the vertical growth of ponderosa pine and soil depth. In the
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Before successful fire exclusion, temperature and precipitation patterns combined with natural and human ignitions allowed fires to burn the dry ponderosa pine forests at relatively frequent (e.g., < 40 years) intervals, even as frequent as every 6.5 years in Arizona.
162:, 40-50 percent of the precipitation occurs in the warmest months. In the middle to southern Rockies, 66 to 75 percent occurs in the warmest months. In the southern areas and those at low elevations, precipitation during the frost-free season is only 20 percent of the 669:
of eastern Oregon, pine stands occupy mollisols. In the Middle and Southern Rocky Mountains, pines and associates are on mollisols, aridisols, entisols, and alfisols. Pine stands in the Gila Mountains are largely on mollisols. The small stands of pine in the
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Graham, Russell T; McCaffrey, Sarah; Jain, Theresa B (2004). Science basis for changing forest structure to modify wildfire behavior and severity (Report). Fort Collins, CO: Rocky Mountain Research Station; US Forest Service. General Technical Report
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concentrations of ponderosa pine (20,700 km or 5,100,000 acres) closely followed by Oregon with 19,000 km (4,700,000 acres) and, when combined, Arizona and New Mexico contain an additional 25,000 km (6,200,000 acres) of ponderosa pine.
1495:. In Vance, RK; Edminster, CB; Covington, WW; Blake, J (eds.). Ponderosa pine ecosystems restoration and conservation: steps toward stewardship (Report). Fort Collins, CO: Rocky Mountain Research Station, US Forest Service. pp. 9–18. RMRS-P-22. 765:) were insects associated with regularly burned areas. In most years bark beetles occurred at endemic levels in ponderosa pine, Douglas-fir, and grand fir killing large and weakened trees that were struck by lightning, infected by root disease ( 614:, pine growth response has been related to soil type, effective soil depth, landform, and moisture availability. Increased water at a site increased plant growth regardless of the soil type and landform. The high water tables associated with 740:
The dense stands that developed increased the abundance of insect and disease epidemics, and when combined with fire exclusion, significantly altered the composition and structure of these forests. Historically, western pine beetle
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or with an understory of shrubs of low to medium height. In perhaps 60 percent of the area, the idealized open character of the ponderosa pine ecosystem has changed to that of a dense and growth-retarded stand, particularly in the
1014: 909: 858: 280:). These species, in particular, exemplify aggressive survivors after disturbance (e.g., fire, mechanical site preparation) and are strong competitors for light and nutrients which compete with ponderosa pine seedlings. 392:) rapidly colonize sites after disturbance and are also active nitrogen fixers. Mid-seral shrubs include Rocky Mountain maple which readily survives disturbances and is joined by late-seral species such as huckleberry ( 261:
of Colorado, in Utah, and in southern Idaho. They also occur along the western slopes of the Sierra Nevadas in California and the eastern slopes of the Cascades in Oregon. Ground-level vegetation includes ninebark
404:). The latter readily survives disturbances but is an aggressive colonizer. Probably one of the greatest competitors and survivors after disturbance of any ground-level species occurring with ponderosa pine is 1401:
Covington, WW; Moore, MM (1994). "Postsettlement changes in natural fire regimes and forest structure: Ecological restoration of old-growth ponderosa pine forests". In Sampson, R. Neil; Adams, David L (eds.).
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Mauk, RL; Henderson, JA (1984). Coniferous forest habitat types of northern Utah (Report). Ogden, UT: Intermountain Forest and Range Experiment Station, US Forest Service. General Technical Report GTR-INT-170.
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The wettest forests where ponderosa pine occurs are the wet grand fir and/or white fir PVTs and the driest western redcedar PVTs. Such forests occur in the interior northwestern United States and in southern
1075:. Proceedings of the symposium management and productivity of western Montana forest soils. Ogden, UT: Intermountain Research Station: US Forest Service. pp. 101–109. General Technical Report INT-280. 425:
and ecological dynamics can cause some problems in maintaining good delineation of the ponderosa pine ecosystem. This ecosystem is idealized as open and parklike with an excellent ground cover of grasses,
809:. In addition to ponderosa pine being damaged by insects, dense stands of Douglas-fir and grand fir or white fir that developed on many settings arevery susceptible to both defoliators and root diseases. 653:
at the northern edge of the Columbia Plateau and in much of the Northern Rocky Mountains, pine and the related forest types occur on inceptisols; the soils of the rest of these areas are largely
1708:. Crossing the Millennium: Integrating spatial technologies and ecological principles for a new age in fire management. Spokane, WA: International Association of Wildland Fire. pp. 179–189. 187:
Ponderosa pine forest can occur in different types of ecological site. Each of these sites can be characterized by its potential vegetation type (PVT) after succession reaches equilibrium or
1852: 1453:. Pacific Northwest forest and rangeland soil organism symposium. Portland, OR: Pacific Northwest Research Station, US Forest Service. pp. 137–145. General Technical Report PNW-GTR-461. 131:
Ponderosa pine forest occurs when the average mean temperature is between 42 and 50 °F (6 and 10 °C) and the July/August mean temperature is 62 to 70 °F (17 to 21 °C).
408:. This ground-level vegetation can play critical roles in forests such as providing wildlife habitat, stabilizing soil, and capturing nutrients after disturbance. For example, fireweed ( 1862: 1857: 1877: 1752:
Wu, Y; Johnson, DW; Angwin, PA (1996). Identification of Armillaria species in Rocky Mountain Region (Report). Golden, CO: Rocky Mountain Region, US Forest Service. Report R2-58.
1108:(Report). Vol. II, assessments and scientific basis for management options. Davis, CA: University of California, Centers for Water and Wildland Resources. pp. 627–662. 1763:
Hedden, R; Barras, S; Coster, J (1981). Hazard-rating system in forest insect pest management (Report). Washington, DC: US Forest Service. General Technical Repport GTR-WO-27.
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Everett, RL; Schellhaas, R; Keenum, D; Spurbeck, D; Olson, P (2000). "Fire history in the ponderosa pine/Douglas-fir forests on the east slope of the Washington Cascades".
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Brawn, JD; Balda, RP (1988). "The influence of silvicultural activity on ponderosa pine forest bird communities in the southwestern United States". In Jackson, JA (ed.).
1633:(Report). Portland, OR: Pacific Northwest Forest and Range Experiment Station, Forest Service U.S. Department of Agriculture. General Technical Report PNW-97. 775:
After a century of fire suppression, these same insects have occurred at epidemic levels in some locations. Ponderosa pine continues to be susceptible to the
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Stein, SJ (1988). "Explanations of imbalanced age structure and scattered distribution of ponderosa pine within a high-elevation mixed coniferous forest".
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Tree species composition change: forest soil organism interaction: potential effects of nutrient cycling and conservation processes in interior forests
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Speer, James H; Swetnam, Thomas W; Wickman, Boyd E; Youngblood, Andrew (2001). "Changes in pandora moth outbreak dynamics during the past 622 years".
1303: 1025:. Proceedings of the Symposium on Ponderosa Pine: Issues, Trends, and Management. US Forest Service. USDA Forest Service Gen. Tech. Rep. PSW-GTR-198. 112:
true forest sites, it occupies low mountains and foothills in many places; yet in mixtures with other species, it is found at moderate elevations.
1872: 360:. The western redcedar PVT is by far the most productive type on which ponderosa pine occurs, and lush and complex vegetation mixes may develop. 863: 793:) defoliates ponderosa pine and scattered outbreaks have occurred in Arizona, California, Colorado, and Oregon during the 20th century. The 823: 939:. Proceedings of the symposium on ponderosa pine: the species and its management. Pullman, WA: Washington State University. pp. 1–6. 194:
In the southern and extreme eastern portion of the range, ponderosa pine grows primarily on ponderosa pine PVTs. On these settings,
1493:"Cheesman Lake a historical ponderosa pine landscape guiding restoration in the South Platte watershed of the Colorado Front Range" 1070: 787:
is more abundant and destructive with some of the severest outbreaks occurring on low-elevation ponderosa pine PVTs. Pandora moth (
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are early-seral associates of ponderosa pine on these sites. These ponderosa pine forests occur in the Rocky Mountains along the
146:. In general, in much of the northern area the frost-free period is 120 days, whereas in many foothill areas and in parts of the 1444:
Harvey, Alan E; Graham, Russell T; McDonald, Gerald I (1999). Meurisse, Robert T; Ypsllantis, William G; Seybold, Cathy (eds.).
1055:(Report). Ogden, UT: Intermountain Forest and Range Experiment Station, US Forest Service. General Technical Report GTR-INT-187. 1704:
Harvey, Alan E; Graham, Russell T; McDonald, Gerald I; Larsen, Michael J (2000). Neuenschwander, Leon F; Ryan, Kevin C (eds.).
1867: 503: 1630: 1161:(Report). Ogden, UT: Intermountain Forest and Range Experiment Station, US Forest Service. General Technical Report INT-144. 1793:(Report). Fort Collins, CO: Rocky Mountain Forest and Range Experimental Station, US Forest Service. Research Note RM-515. 828: 370:). A rich understory of shrubs, grasses, and forbs occur in these forests. Early seral-species such as redstem ceanothus ( 1069:
Jurgensen, Martin F; Tonn, Jonalea T; Graham, Russell T; Harvey, Alan E; Geier-Hayes, Kathleen (1991). Harvey, AE (ed.).
1040:(Report). Fort Collins, CO: Rocky Mountain Forest and Range Experiment Station, US Forest Service. Research Paper RM-276. 84:
forests. Understory species depends on location. Fire suppression has led to insect outbreaks in ponderosa pine forests.
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Local topography can be gentle, as on plateau tops and low mountains, or it can be steep, as on canyon walls and faces.
166:. In northern areas precipitation during the growing season may be as high as 40 percent of the evaporation potential. 1808:(Report). Portland, OR: Pacific Northwest Research Station, US Forest Service. General Technical Report PNW-GTR-327. 1726:(Report). Portland, OR: Pacific Northwest Research Station, US Forest Service. General Technical Report PNW-GTR-327. 1543:
Cooper, CF (1960). "Changes in vegetation, structure, and growth of southwest pine forests since white settlement".
1513:(Report). Portland, OR: Pacific NorthwestResearch Station, US Forest Service. General Technical Report PNW-GTR-462. 1666:. Vol. 3. Madison, WI: The International Council for Bird Preservation, United States Section. pp. 3–21. 1136:
An assessment of ecosystem components in the interior Columbia Basin and portions of the Klamath and Great Basins
570: 1832: 1322: 1468:(Report). Ogden, UT: Rocky Mountain Research Station, US Forest Service. General Technical Report RMRS-GTR-114. 1038:
Forest vegetation of the Black Hills National Forest of South Dakota and Wyoming: a habitat type classification
692: 159: 135: 1233:(Report). Ogden, UT: Intermountain Research Station, US Forest Service. General Technical Report INT-GTR-363. 743: 662: 558: 534: 447: 410: 330: 276: 179: 1806:
Historical and current roles of insects and pathogens in eastern Oregon and Washington forested landscapes
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Historical and current roles of insects and pathogens in eastern Oregon and Washington forested landscapes
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Schroeder, Herbert (2002). "Experiencing nature in special places: surveys in the north central region".
1197:(Report). Ogden, UT: Intermountain Research Station, US Forest Service. General Technical Report INT-236. 1138:. Vol. II. Portland, OR: Pacific Northwest Research Station, US Forest Service. pp. 338–1055. 234: 163: 24: 1595: 1552: 1364: 1253: 780: 761: 566: 479: 400: 372: 347: 311: 242:
properties which is the process of making elemental nitrogen in the atmosphere available to plants.
776: 451: 378: 1304:"Determining reference conditions for ecosystem management of southwestern ponderosa pine forests" 915: 687: 1649:
Management of ponderosa pine in the southwest as developed by research and experimental practices
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Barrett, SW; Arno, SF (1982). "Indian fires as an ecological influence in the Northern Rockies".
1269: 1020: 650: 615: 582: 538: 530: 483: 463: 361: 789: 666: 626: 542: 436: 366: 305: 92: 1828: 1686: 1603: 1560: 1426: 1372: 1318: 1261: 1139: 725: 704: 622: 574: 562: 554: 550: 546: 526: 415: 357: 188: 65: 61: 30: 783:. These beetles often kill ponderosa pine on Douglas-fir and grand fir/white fir PVTs. The 521:
The most abundant and important resident birds in the ponderosa pine ecosystem include the
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are the climax species. Additional trees that can occur in such forests include juniper (
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Van Hooser, Dwane; Keegan, Charles E III (1988). Baumgartner, DM; Lotan, JE (eds.).
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and ninebark are frequent associates, but tall shrubs such as Rocky Mountain maple (
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Silviculture of ponderosa pine in the Pacific Northwest: the state of our knowledge
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Keith, James O. (1965). "The Abert Squirrel and Its Dependence on Ponderosa Pine".
921:. Washington D.C.: US Forest Service. pp. 21–22. Agriculture Handbook No. 475. 784: 749: 607: 335: 299: 270: 120: 1215:. Pullman, WA: Washington Agricultural Experiment Station. Technical Bulletin 60. 1791:
Stand density and mountain pine beetle-caused tree mortality in ponderosa stands
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Rasmussen, D Irvin (1941). "Biotic communities of the Kaibab plateau, Arizona".
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Hann, Wendel J; Jones, Jeffrey L.; Karl; Sherm, Michael G.; et al. (1997).
1052: 1037: 671: 645:. In northern and eastern California, ponderosa pine stands are associated with 603: 598: 264: 258: 246: 73: 35: 1492: 19: 767: 634: 578: 495: 216: 618:
tend to increase site productivity regardless of the soil type and landform.
610:, soil depth had more influence on tree height than soil parent material. In 511: 499: 467: 405: 394: 293: 288: 284: 143: 81: 77: 1355:
Stewart, OC (1951). "Burning and natural vegetation in the United States".
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With increasing moisture, ponderosa pine occurs as a mid-seral species and
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is a frequent associate of ponderosa pine with an occasional paper birch (
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has a rather wide range of adaptability and can dominate some of the less
1230: 755: 642: 630: 514:. The Kaibab squirrel is rare and endemic to this ecosystem on Arizona's 139: 119:, low mountain sites are common, but it is difficult to characterize the 116: 1805: 1465: 1143: 1615: 1572: 1273: 798: 733: 696: 658: 654: 646: 638: 611: 422: 283:
Ponderosa pine forests in the north can occur in dry forests where the
210: 204: 155: 39: 1384: 916:"Vegetation and environmental features of forest and range ecosystems" 806: 802: 794: 487: 475: 459: 228: 72:, while in the more northern part of its range, it can transition to 1607: 1564: 1265: 1376: 1157:
Steele, R; Cooper, SV; Ondov, DM; Roberts, DW; Pfister, RD (1983).
1651:. Washington, DC: US Forest Service; 218. Agriculture Monograph 6. 1179:. Pullman, WA: Cooperative Extension, Washington State University. 719: 686: 446: 427: 341: 173: 91: 29: 18: 138:
season at any location in the ecosystem depends largely upon the
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Hessburg, Paul F; Mitchell, Russel G; Filip, Gregory M (1994).
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Hessburg, Paul F; Mitchell, Russel G; Filip, Gregory M (1994).
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Fire/decay: managing codependent processes across the landscape
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Forest habitat types of northern Idaho: a second approximation
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Result of prescribed burn in the ponderosa pine forest of the
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Kaufmann, MR; Fornwalt, PJ; Huckaby, LS; Stoker, JM (2001).
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Assessment of late successional forests of the Sierra Nevada
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Coniferous forest habitat types of central and southern Utah
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10.1890/0012-9658(2001)082[0679:CIPMOD]2.0.CO;2
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10.1890/1051-0761(1997)007[0895:DRCFEM]2.0.CO;2
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Fire ecology of the forest habitat types of northern Idaho
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Forest vegetation of eastern Washington and northern Idaho
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Baumgartner, DM; Boyd, RJ; Breuer, DW; Miller, DL (1986).
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Williams, RE; Shaw, CG III; Wargo, PM; Sites, WH (1986).
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Weed control for forest productivity in the Interior West
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Sierra Nevada ecosystem project, final report to Congress
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Nitrogen fixation in forest soils of the inland northwest
238:), a frequent shrub in these forests, stands out for its 593:
Ponderosa pine grows on a variety of soils ranging from
561:. Birds that are common during the summer include the 351:
grows in the understory of some ponderosa pine forests
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can aggressively compete with ponderosa pine seedlings
68:. In the south and east, ponderosa pine forest is the 1778:. Ogden, UT: Intermountain Region, US Forest Service. 1159:
Forest habitat types of eastern Idaho-western Wyoming
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tree species. Ground-level vegetation includes oaks (
1406:. New York: The Haworth Press Inc. pp. 153–181. 1404:
Assessing forest ecosystem health in the Inland West
1134:. In Quigley, Thomas M; Arbelbide, Sylvia J (eds.). 937:
Distributions and volumes of ponderosa pine forests
1170: 1168: 249:becomes the late-seral species (Douglas-fir PVT). 1853:Temperate coniferous forests of the United States 1206: 1204: 1097:Franklin, Jerry F; Fites-Kaufman, Jo Ann (1996). 1741:. Washington, DC: US Forest Service. leaflet 78. 732:In the western United States domestic livestock 1229:Smith, Jane Kapler; Fischer, William C (1997). 1064: 1062: 16:Plant community where Pinus ponderosa is common 1863:Natural history of the California Coast Ranges 1858:Plant communities of the Western United States 1642: 1640: 1508:Place assessment: how people define ecosystems 1396: 1394: 454:is only found in mature ponderosa pine forest. 1506:Galliano, Steven J; Loeffler, Gary M (1999). 1188: 1186: 1004: 1002: 1000: 998: 996: 994: 992: 990: 988: 986: 984: 982: 980: 978: 976: 974: 972: 970: 968: 966: 8: 1878:Forests of the Sierra Nevada (United States) 1774:Gardner, B; Mocettini, P; Halsey, D (1997). 1224: 1222: 1193:Cooper, SV; Neiman, KE; Roberts, DW (1991). 964: 962: 960: 958: 956: 954: 952: 950: 948: 946: 930: 928: 123:of the ecosystem because it varies greatly. 1302:Fulé, PZ; Covington, WW; Moore, MM (1997). 1125: 1123: 1121: 1119: 1117: 1115: 1019:Graham, Russell T; Jain, Theresa B (2005). 819:Maritime Coast Range Ponderosa Pine forests 458:In the ponderosa pine ecosystem, the major 865:General Information: Ponderosa Pine Forest 1289:Fire ecology of Pacific Northwest forests 848: 846: 844: 478:. Animals of less importance include the 914:Garrison, George A; et al. (1977). 797:prefer loose soils created by weathered 220:spp.), and low shrubs (e.g., snowberry ( 1146:. General Technical Report PNW-GTR-405. 899: 897: 895: 893: 891: 889: 887: 885: 840: 1776:Forest, insect, and disease conditions 1211:Daubenmire, R; Daubenmire, JB (1968). 7: 824:Rocky Mountain ponderosa pine forest 1036:Hoffman, GR; Alexander, RR (1987). 14: 1132:"Landscape dynamics of the Basin" 1051:Youngblood, AP; Mauk, RL (1985). 1013: This article incorporates 1008: 908: This article incorporates 903: 857: This article incorporates 852: 1291:. Washington, DC: Island Press. 1873:Forests of the Rocky Mountains 621:Along the western edge of the 504:golden-mantled ground squirrel 1: 1789:Schmid, JM; Mata, SA (1992). 1679:Forest Ecology and Management 1431:10.1016/S0378-1127(99)00168-1 1419:Forest Ecology and Management 829:California Floristic Province 759:), Douglas-fir tussock moth ( 398:spp.) and false huckleberry ( 232:spp.)). Russet buffaloberry ( 1691:10.1016/0378-1127(88)90125-9 870:United States Forest Service 198:is the most frequent early- 96:Range map of ponderosa pine 48:is a plant association and 1894: 1464:Graham, Russell T (2003). 625:and the east slope of the 1739:Forest insect and disease 1629:Barrett, James W (1979). 1022:Ponderosa Pine Ecosystems 728:affected by bark beetles 724:Ponderosa pine stand in 693:Coconino National Forest 629:, common soil types are 376:), snowbrush ceanothus ( 160:Northern Rocky Mountains 1311:Ecological Applications 744:Dendroctonus brevicomis 559:western red-tailed hawk 535:Rocky Mountain nuthatch 411:Chamerion angustifolium 277:Calamagrostis rubescens 180:Calamagrostis rubescens 60:. It is found from the 1466:Hayman Fire case study 1287:Agee, James K (1993). 1015:public domain material 910:public domain material 859:public domain material 805:where they burrow and 729: 699: 571:Williamson's sapsucker 455: 352: 184: 97: 42: 34:Ponderosa forest near 27: 23:Ponderosa forest near 1868:Forests of California 1588:Ecological Monographs 1545:Ecological Monographs 772:trees were stressed. 753:spp.), fir engraver ( 723: 690: 450: 345: 235:Shepherdia canadensis 177: 164:evaporation potential 95: 56:and found in western 46:Ponderosa pine forest 33: 25:Forest Lakes, Arizona 22: 1647:Pearson, GA (1950). 785:pine engraver beetle 781:mountain pine beetle 762:Orgyia pseudotsugata 480:bushy-tailed woodrat 401:Menziesia ferruginea 373:Ceanothus sanguineus 348:Ceanothus sanguineus 312:Calocedrus decurrens 297:spp.), pinyon pine ( 1600:1941EcoM...11..229R 1557:1960EcoM...30..129C 1526:Journal of Forestry 1369:1951GeoRv..41..317S 1357:Geographical Review 1338:Journal of Forestry 1258:1965Ecol...46..150K 1144:10.2737/PNW-GTR-405 777:western pine beetle 382:) and Sitka alder ( 379:Ceanothus velutinus 274:), and pine grass ( 756:Scolytus ventralis 747:), pine engraver ( 730: 700: 674:are on aridisols. 651:Okanogan Highlands 583:band-tailed pigeon 547:redshafted flicker 539:mountain chickadee 531:sharp-shinned hawk 484:white-footed mouse 464:Rocky Mountain elk 456: 362:Western white pine 353: 309:), incense-cedar ( 268:spp.), elk sedge ( 226:spp.) and spirea ( 185: 134:The length of the 98: 43: 28: 1664:Bird conservation 790:Coloradia pandora 667:Wallowa Mountains 627:Cascade Mountains 567:Audubon's warbler 437:Pacific Northwest 367:Betula papyrifera 306:Pinus lambertiana 1885: 1837: 1836: 1816: 1810: 1809: 1801: 1795: 1794: 1786: 1780: 1779: 1771: 1765: 1764: 1760: 1754: 1753: 1749: 1743: 1742: 1734: 1728: 1727: 1725: 1716: 1710: 1709: 1701: 1695: 1694: 1674: 1668: 1667: 1659: 1653: 1652: 1644: 1635: 1634: 1626: 1620: 1619: 1583: 1577: 1576: 1540: 1534: 1533: 1521: 1515: 1514: 1512: 1503: 1497: 1496: 1488: 1482: 1481: 1476: 1470: 1469: 1461: 1455: 1454: 1452: 1441: 1435: 1434: 1425:(1–3): 207–225. 1414: 1408: 1407: 1398: 1389: 1388: 1352: 1346: 1345: 1333: 1327: 1326: 1308: 1299: 1293: 1292: 1284: 1278: 1277: 1252:(1/2): 150–163. 1241: 1235: 1234: 1226: 1217: 1216: 1208: 1199: 1198: 1190: 1181: 1180: 1172: 1163: 1162: 1154: 1148: 1147: 1127: 1110: 1109: 1103: 1094: 1088: 1087: 1083: 1077: 1076: 1066: 1057: 1056: 1048: 1042: 1041: 1033: 1027: 1026: 1012: 1011: 1006: 941: 940: 932: 923: 922: 920: 907: 906: 901: 880: 879: 877: 876: 856: 855: 850: 726:British Columbia 705:Cultural burning 623:Columbia Plateau 575:chipping sparrow 563:western bluebird 555:northern goshawk 551:red-backed junco 527:long-crested jay 452:Abert's squirrel 358:British Columbia 319:, Jeffrey pine ( 208:spp.), grasses ( 189:climax community 62:British Columbia 1893: 1892: 1888: 1887: 1886: 1884: 1883: 1882: 1843: 1842: 1841: 1840: 1818: 1817: 1813: 1803: 1802: 1798: 1788: 1787: 1783: 1773: 1772: 1768: 1762: 1761: 1757: 1751: 1750: 1746: 1736: 1735: 1731: 1723: 1718: 1717: 1713: 1703: 1702: 1698: 1676: 1675: 1671: 1661: 1660: 1656: 1646: 1645: 1638: 1628: 1627: 1623: 1608:10.2307/1943204 1585: 1584: 1580: 1565:10.2307/1948549 1542: 1541: 1537: 1523: 1522: 1518: 1510: 1505: 1504: 1500: 1490: 1489: 1485: 1478: 1477: 1473: 1463: 1462: 1458: 1450: 1443: 1442: 1438: 1416: 1415: 1411: 1400: 1399: 1392: 1354: 1353: 1349: 1335: 1334: 1330: 1306: 1301: 1300: 1296: 1286: 1285: 1281: 1266:10.2307/1935266 1243: 1242: 1238: 1228: 1227: 1220: 1210: 1209: 1202: 1192: 1191: 1184: 1174: 1173: 1166: 1156: 1155: 1151: 1129: 1128: 1113: 1101: 1096: 1095: 1091: 1085: 1084: 1080: 1068: 1067: 1060: 1050: 1049: 1045: 1035: 1034: 1030: 1018: 1009: 1007: 944: 934: 933: 926: 918: 913: 904: 902: 883: 874: 872: 862: 853: 851: 842: 837: 815: 718: 685: 680: 591: 508:Kaibab squirrel 445: 339:) often occur. 303:), sugar pine ( 240:nitrogen fixing 172: 152:Gila Wilderness 129: 90: 66:Durango, Mexico 50:plant community 17: 12: 11: 5: 1891: 1889: 1881: 1880: 1875: 1870: 1865: 1860: 1855: 1845: 1844: 1839: 1838: 1827:(3): 679–697. 1811: 1796: 1781: 1766: 1755: 1744: 1729: 1711: 1696: 1685:(2): 139–153. 1669: 1654: 1636: 1621: 1594:(3): 229–275. 1578: 1551:(2): 129–164. 1535: 1516: 1498: 1483: 1471: 1456: 1436: 1409: 1390: 1377:10.2307/211026 1363:(2): 317–320. 1347: 1344:(10): 647–651. 1328: 1317:(3): 895–908. 1294: 1279: 1236: 1218: 1200: 1182: 1164: 1149: 1111: 1089: 1078: 1058: 1043: 1028: 942: 924: 881: 839: 838: 836: 833: 832: 831: 826: 821: 814: 811: 717: 714: 684: 681: 679: 676: 590: 587: 543:Cassin's finch 523:pygmy nuthatch 516:Kaibab Plateau 444: 441: 421:The impact of 327:lodgepole pine 322:Pinus jeffreyi 255:lodgepole pine 223:Symphoricarpos 171: 168: 128: 125: 106:ponderosa pine 89: 86: 54:ponderosa pine 15: 13: 10: 9: 6: 4: 3: 2: 1890: 1879: 1876: 1874: 1871: 1869: 1866: 1864: 1861: 1859: 1856: 1854: 1851: 1850: 1848: 1834: 1830: 1826: 1822: 1815: 1812: 1807: 1800: 1797: 1792: 1785: 1782: 1777: 1770: 1767: 1759: 1756: 1748: 1745: 1740: 1733: 1730: 1722: 1715: 1712: 1707: 1700: 1697: 1692: 1688: 1684: 1680: 1673: 1670: 1665: 1658: 1655: 1650: 1643: 1641: 1637: 1632: 1625: 1622: 1617: 1613: 1609: 1605: 1601: 1597: 1593: 1589: 1582: 1579: 1574: 1570: 1566: 1562: 1558: 1554: 1550: 1546: 1539: 1536: 1531: 1527: 1520: 1517: 1509: 1502: 1499: 1494: 1487: 1484: 1480:RMRS-GTR-120. 1475: 1472: 1467: 1460: 1457: 1449: 1448: 1440: 1437: 1432: 1428: 1424: 1420: 1413: 1410: 1405: 1397: 1395: 1391: 1386: 1382: 1378: 1374: 1370: 1366: 1362: 1358: 1351: 1348: 1343: 1339: 1332: 1329: 1324: 1320: 1316: 1312: 1305: 1298: 1295: 1290: 1283: 1280: 1275: 1271: 1267: 1263: 1259: 1255: 1251: 1247: 1240: 1237: 1232: 1225: 1223: 1219: 1214: 1207: 1205: 1201: 1196: 1189: 1187: 1183: 1178: 1171: 1169: 1165: 1160: 1153: 1150: 1145: 1141: 1137: 1133: 1126: 1124: 1122: 1120: 1118: 1116: 1112: 1107: 1100: 1093: 1090: 1082: 1079: 1074: 1073: 1065: 1063: 1059: 1054: 1047: 1044: 1039: 1032: 1029: 1024: 1023: 1016: 1005: 1003: 1001: 999: 997: 995: 993: 991: 989: 987: 985: 983: 981: 979: 977: 975: 973: 971: 969: 967: 965: 963: 961: 959: 957: 955: 953: 951: 949: 947: 943: 938: 931: 929: 925: 917: 911: 900: 898: 896: 894: 892: 890: 888: 886: 882: 871: 867: 866: 860: 849: 847: 845: 841: 834: 830: 827: 825: 822: 820: 817: 816: 812: 810: 808: 804: 800: 796: 792: 791: 786: 782: 778: 773: 770: 769: 764: 763: 758: 757: 752: 751: 746: 745: 738: 735: 727: 722: 715: 713: 709: 706: 698: 694: 689: 682: 677: 675: 673: 668: 664: 660: 656: 652: 648: 644: 640: 636: 632: 628: 624: 619: 617: 613: 609: 605: 600: 596: 588: 586: 584: 580: 576: 572: 568: 564: 560: 556: 552: 548: 544: 540: 536: 532: 528: 524: 519: 517: 513: 509: 505: 501: 497: 493: 492:rock squirrel 489: 485: 481: 477: 473: 472:mountain lion 469: 465: 461: 453: 449: 442: 440: 438: 433: 429: 424: 419: 417: 413: 412: 407: 403: 402: 397: 396: 391: 387: 386: 385:Alnus viridis 381: 380: 375: 374: 369: 368: 363: 359: 350: 349: 344: 340: 338: 337: 332: 328: 324: 323: 318: 317:western larch 314: 313: 308: 307: 302: 301: 296: 295: 290: 286: 281: 279: 278: 273: 272: 267: 266: 260: 256: 252: 251:Quaking aspen 248: 243: 241: 237: 236: 231: 230: 225: 224: 219: 218: 213: 212: 207: 206: 201: 197: 196:quaking aspen 192: 190: 182: 181: 176: 169: 167: 165: 161: 157: 153: 149: 148:Sierra Nevada 145: 141: 137: 132: 126: 124: 122: 118: 113: 111: 107: 102: 94: 87: 85: 83: 79: 75: 71: 70:climax forest 67: 63: 59: 58:North America 55: 52:dominated by 51: 47: 41: 37: 32: 26: 21: 1824: 1820: 1814: 1799: 1784: 1775: 1769: 1758: 1747: 1738: 1732: 1714: 1705: 1699: 1682: 1678: 1672: 1663: 1657: 1648: 1624: 1591: 1587: 1581: 1548: 1544: 1538: 1529: 1525: 1519: 1501: 1486: 1474: 1459: 1446: 1439: 1422: 1418: 1412: 1403: 1360: 1356: 1350: 1341: 1337: 1331: 1314: 1310: 1297: 1288: 1282: 1249: 1245: 1239: 1212: 1176: 1152: 1135: 1105: 1092: 1081: 1071: 1046: 1031: 1021: 936: 873:. Retrieved 864: 788: 774: 766: 760: 754: 748: 742: 739: 731: 710: 701: 678:Disturbances 620: 608:South Dakota 592: 520: 457: 420: 409: 399: 393: 389: 383: 377: 371: 365: 354: 346: 336:Acer glabrum 334: 320: 310: 304: 300:Pinus edulis 298: 292: 282: 275: 271:Carex geyeri 269: 263: 244: 233: 227: 221: 215: 209: 203: 193: 186: 178: 133: 130: 121:physiography 114: 103: 99: 88:Physiography 45: 44: 708:intervals. 672:Great Basin 635:inceptisols 604:Black Hills 599:sedimentary 265:Physocarpus 259:Front Range 247:Douglas-fir 74:Douglas-fir 36:Mormon Lake 1847:Categories 1532:(5): 8–14. 875:2023-06-16 835:References 768:Armillaria 579:horned owl 573:, western 496:cottontail 217:Andropogon 170:Vegetation 136:frost-free 661:. In the 649:. In the 643:aridisols 631:mollisols 512:chipmunks 500:porcupine 468:mule deer 406:pinegrass 395:Vaccinium 331:Pinegrass 294:Juniperus 289:white fir 285:grand fir 144:elevation 82:white fir 78:grand fir 813:See also 799:granites 683:Wildfire 659:entisols 655:alfisols 647:ultisols 639:entisols 595:volcanic 462:are the 150:and the 140:latitude 117:Semiarid 1821:Ecology 1616:1943204 1596:Bibcode 1573:1948549 1553:Bibcode 1365:Bibcode 1274:1935266 1254:Bibcode 1246:Ecology 734:grazing 697:Arizona 616:springs 612:Montana 460:mammals 423:logging 416:mosaics 390:sinuata 325:), and 211:Festuca 205:Quercus 156:Arizona 127:Climate 40:Arizona 1614:  1571:  1385:211026 1383:  1272:  807:pupate 803:pumice 795:larvae 641:, and 581:, and 557:, and 510:, and 488:bobcat 476:coyote 474:, and 430:, and 428:sedges 229:Spirea 104:Since 1724:(PDF) 1612:JSTOR 1569:JSTOR 1511:(PDF) 1451:(PDF) 1381:JSTOR 1307:(PDF) 1270:JSTOR 1102:(PDF) 1017:from 919:(PDF) 912:from 861:from 716:Other 589:Soils 443:Fauna 432:forbs 388:ssp. 200:seral 110:mesic 80:, or 779:and 665:and 663:Blue 657:and 253:and 214:and 142:and 1829:doi 1687:doi 1604:doi 1561:doi 1530:100 1427:doi 1423:129 1373:doi 1319:doi 1262:doi 1140:doi 801:or 750:Ips 606:of 597:to 315:), 287:or 154:in 76:or 64:to 1849:: 1825:82 1823:. 1683:25 1681:. 1639:^ 1610:. 1602:. 1592:11 1590:. 1567:. 1559:. 1549:30 1547:. 1528:. 1421:. 1393:^ 1379:. 1371:. 1361:41 1359:. 1342:80 1340:. 1313:. 1309:. 1268:. 1260:. 1250:46 1248:. 1221:^ 1203:^ 1185:^ 1167:^ 1114:^ 1104:. 1061:^ 945:^ 927:^ 884:^ 868:. 843:^ 695:, 637:, 633:, 585:. 577:, 569:, 565:, 553:, 549:, 545:, 541:, 537:, 533:, 529:, 525:, 518:. 506:, 502:, 498:, 494:, 490:, 486:, 482:, 470:, 466:, 439:. 418:. 329:. 191:. 38:, 1835:. 1831:: 1693:. 1689:: 1618:. 1606:: 1598:: 1575:. 1563:: 1555:: 1433:. 1429:: 1387:. 1375:: 1367:: 1325:. 1321:: 1315:7 1276:. 1264:: 1256:: 1142:: 878:. 741:( 262:(

Index


Forest Lakes, Arizona

Mormon Lake
Arizona
plant community
ponderosa pine
North America
British Columbia
Durango, Mexico
climax forest
Douglas-fir
grand fir
white fir

ponderosa pine
mesic
Semiarid
physiography
frost-free
latitude
elevation
Sierra Nevada
Gila Wilderness
Arizona
Northern Rocky Mountains
evaporation potential

Calamagrostis rubescens
climax community

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