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Draft. A draft ecological site description is either incomplete or has not undergone quality control and quality assurance review.
MLRA notes
Major Land Resource Area (MLRA): 022A–Sierra Nevada and Tehachapi Mountains
This ESD was developed using older policy requirements which have been improved with the intent of improving ESD products overall. Users should approach these materials with some caution as the content herein, while likely useful for some purposes, was developed within parameters now recognized as needing varying levels of improvement. As always, a site-specific investigation is highly recommended when site-specific management alternatives are to be developed and/or management decisions are to be made.
Each ESD is an interpretation of the ecological relationships between biotic and abiotic aspects of the landscape. Users of this document should be aware of the limitations of this tool to the extent that specific local conditions may not be entirely captured within the ESD. In particular, management decisions should be supported by site-specific inventories, assessments and planning processes based on the best available information including and extending beyond the ESD.
An ESD is not a permanent determination of ecological dynamics. Rather, each ESD is an evolving body of work intrinsically tied to the soil surveys and data associated with soil map unit components of correlated soil-ecological site relationships. As new information becomes available, updates may be made or may be underway at any given time. Minor updates may be made without announcement when such changes do not modify the ecological site concept, the soils correlated or the state-and-transition model.
Table 1. Dominant plant species
Tree (1) Populus tremuloides
Shrub (1) Salix
Herbaceous (1) Elymus trachycaulus ssp. trachycaulus
Physiographic features
This forest site occurs on terraces immediately adjacent to spring-fed, perennial, mountain streams. Slopes range from 0 to 8 percent, but are typically 2 to 4 percent. Elevations are 6500 to over 9000 feet.
Table 2. Representative physiographic features
Landforms (1) Stream terrace
Flooding duration Extremely brief (0.1 to 4 hours) to very brief (4 to 48 hours) Flooding frequency Rare Elevation 6500 – 9000 ft Slope 0 – 8 % Aspect Aspect is not a significant factor Climatic features
The climate is characterized as subhumid-continental with cold, moist winters and cool, dry summers. Average annual precipitation is 14 or more inches. Mean annual air temperature is 40 to 43 degrees F. The average growing season is 70 to 100 days. Climate data used to support this section were derived from PRISM and is not specifically tied to any dominant climate station.
Table 3 Representative climatic features
Frost-free period (average) 100 days Freeze-free period (average) 0 days Precipitation total (average) 40 in BarLineFigure 1. Monthly precipitation range
BarLineFigure 2. Monthly average minimum and maximum temperature
">Influencing water features
This site is associated with spring-fed perennial streams.
Soil features
The soils associated with this site are generally deep to very deep and somewhat poorly drained. These soils have a seasonally high water table within 10 to 20 inches of the surface. The water table normally stabilizes within 30 inches of the surface through a major portion of the growing season. The soils have a thick, dark, medium-textured surface layer. The underlying material is typically medium textured and slightly acid to mildly alkaline in reaction. Available water capacity is high and surface runoff is very slow to slow depending on slope. These soils are susceptible to gullying which intercepts normal overflow patterns causing site degradation.
The soils associated with this site are classified as Aquic Argicryolls, Aquic Cumulic Haploxerolls, and Aquic Haplocryolls
CA693 Tahoe Basin Area, California and Nevada
7401;Burnlake-Roadcat association, 4 to 30 percent slopes;Aquic Haplocryolls
9111;Florand-Lostridge-Fishsnooze association, 15 to 50 percent slopes;Aquic Haplocryolls
9431;Sofgran-Klauspeak-Temo association, 15 to 50 percent slopes;Aquic Haplocryolls
CA724 Eldorado National Forest Area, California, Parts of Alpine, Amador, El Dorado, and Placer Counties
130ty;Sofgran-Klauspeak-Temo association, 15 to 50 percent slopes;Aquic Haplocryolls
240ty;Granylith-Hargran-Rock outcrop complex, 8 to 30 percent slopes;Aquic Haplocryolls
CA729 Toiyabe National Forest Area, California
120;Toiyabe-Corbett-Rock outcrop complex, 30 to 50 percent slopes;Aquic Haplocryolls
122;Toiyabe-Corbett-Rock outcrop complex, 50 to 75 percent slopes;Aquic Haplocryolls
130;Sofgran-Klauspeak-Temo association;Aquic Haplocryolls
140;Temo-Dagget-Rock outcrop complex, 30 to 75 percent slopes;Aquic Haplocryolls
160;Hopeval complex, 2 to 8 percent slopes;Aquic Haplocryolls
170;Burnlake-Roadcat association;Aquic Haplocryolls
171;Stumpatil-Morscour association;Aquic Haplocryolls
190;Hopeval complex, 0 to 2 percent slopes;Aquic Haplocryolls
200;Cavebear-Hopeval complex, 2 to 8 percent slopes;Aquic Haplocryolls
212;Waterpeak-Sofgran-Temo association;Aquic Haplocryolls
220;Hardtil-Alpineco-Rock outcrop complex, 8 to 30 percent slopes;Aquic Haplocryolls
221;Hardtil-Alpineco-Rock outcrop complex, 30 to 75 percent slopes;Aquic Haplocryolls
222;Hardtil-Alpineco-Rock outcrop complex, warm, 8 to 30 percent slopes;Aquic Haplocryolls
230;Hawkinspeak-Thiefridge-Angelwhine association;Aquic Haplocryolls
240;Granylith-Hargran-Rock outcrop complex, 8 to 30 percent slopes;Aquic Haplocryolls
250;Florand-Lostridge-Fishsnooze association;Aquic Haplocryolls
480;Aspetill association;Aquic Argicryolls
481;Aspetill association, very stony;Aquic Argicryolls
490;Cloudburst-Murain association;Aquic Argicryolls
491;Cloudburst-Murain-Hardtil association;Aquic Argicryolls
500;Chrisflat very gravelly coarse sandy loam, 4 to 15 percent slopes;Aquic Cumulic Haploxerolls
520;Canfire-Crispy-Rock outcrop association;Aquic Cumulic Haploxerolls
540;Lostcannon association;Aquic Haplocryolls
560;Dunderberg-Conwayridge association;Aquic Argicryolls
561;Dunderberg association;Aquic Argicryolls
840;Lavaspring-Trespass complex, 0 to 4 percent slopes;Aquic Argicryolls
NV773 Douglas County Area, Nevada
120;Toiyabe-Corbett-Rock outcrop complex, 30 to 50 percent slopes;Aquic Haplocryolls
140;Temo-Dagget-Rock outcrop complex, 30 to 75 percent slopes;Aquic Haplocryolls
Table 4. Representative soil features
Surface texture (1) Very bouldery sandy loam
(2) Very gravelly sandy loam
Family particle size (1) Loamy
Drainage class Somewhat poorly drained Permeability class Moderately rapid Soil depth 72 – 0 in Surface fragment cover <=3" 40 – 45 % Surface fragment cover >3" 10 – 15 % Available water capacity
(0-40in)5.6 – 7.3 in Calcium carbonate equivalent
(0-40in)Not specified Electrical conductivity
(0-40in)Not specified Sodium adsorption ratio
(0-40in)Not specified Soil reaction (1:1 water)
(0-40in)5.6 – 7.3 Subsurface fragment volume <=3"
(Depth not specified)21 – 56 % Subsurface fragment volume >3"
(Depth not specified)10 – 25 % Ecological dynamics
This site is composed of one to several quaking aspen clones, with a common genetic makeup and individual phenological and physiological characteristics.
Major Successional Stages of Woodland Development:
HERBACEOUS: Vegetation is dominated by grasses and forbs under full sunlight. This stage is experienced after a major disturbance such as fire, root-rot, insect damage, beaver activity or tree harvest. Following a major disturbance, the root system gives rise to many root suckers, assuming the root system is intact and healthy. Residual trees left following harvest have little or no affect on the composition and production of the herbaceous vegetation.
SHRUB-HERBACEOUS: Herbaceous vegetation dominates the site. Early sucker growth ranges from less than 1 foot to more than 3 feet per year for shoots having good competitive position. If the aspen stand is healthy, these first two stages will only last from one to two years. However, if competing brush and herbaceous plants grow for a full season before aspen suckers emerge, a reduction in sprouting and the eventual growth and survival of the aspen suckers may occur.
SAPLING: In the absence of disturbance, tree seedlings develop into saplings (20 inches to 4.5 feet in height) with a range in canopy cover of about 15 to 35 percent. Vegetation consists of grasses, forbs and a few shrubs in association with tree saplings.
POLE STAGE: As the canopy closes, trees stratify into crown classes quickly, despite genetic uniformity within clones. Aspen stands are self-thinning, especially at young ages. This stage is characterized by rapid growth of the aspen trees, both in height and canopy cover. The visual aspect and vegetal structure are dominated by aspen ranging from about 10 to 20 feet in height, and having a diameter at breast height of about 2 to 4 inches. Understory vegetation is moderately influenced by a tree canopy of about 35 to over 50 percent.
IMMATURE FOREST: Growth of the aspen slows somewhat during this stage. There is a fairly continual adjustment of trees to growing space, and a loss in competitive position of many trees making up the codominant, intermediate and over-topped classes. When competition becomes intense enough to appreciably affect the diameter growth of dominants, mortality quickly reduces the number of trees in the lower crown classes. There are periodic surges in mortality, with a disproportionate number of trees, mostly those over-topped, dying within a short time. The
NATURE OF THE FOREST COMMUNITY
IMMATURE FOREST: visual aspect and vegetal structure are dominated by quaking aspen greater than 35 feet in height. Understory vegetation is moderately influenced by a tree overstory canopy of about 25 to 40 percent.
MATURE FOREST: The visual aspect and vegetal structure are dominated by single-story, quaking aspen that have reached, or are near, maximal heights for the site. Growth of aspen continues during this stage. Diameter growth shows recovery with the release of competition previously endured during the immature forest stage. Tree heights range from 50 to over 80 feet, depending upon site and clonal genotype. Trees have developed tall, straight, clear stems with short, narrow, dome-like crowns. Tree canopy cover ranges from 25 to 40 percent. Understory vegetation is strongly influenced by tree competition, overstory shading, and duff accumulation. Relatively shade tolerant perennial grasses and forbs form a continuous layer beneath tree canopy. Few vegetative shoots and/or saplings of quaking aspen occur in the understory.
OVER-MATURE FOREST: This stage is normally dominated by aspen that have reached maximal heights for the site. Trees have straight, clear stems. In the absence of naturally occurring disturbances, the tree canopy on this site can become very dense, and is often greater than 50 percent. As less light penetrates below the tree canopy, competitive relationships in the understory vegetation are altered. Although plants in the understory of the over-mature forest are shade tolerant, even these species progressively decrease in abundance and productivity as tree canopy cover increases.
Over-mature aspen stands slowly die. As openings in the overstory are created through tree mortality, otherwise inconspicuous aspen suckers emerge on the forest floor. These suckers typically arise over a period of several years and the resulting stand is broadly even-aged. As even-aged stands reach old age without disturbance, stand deterioration is likely to extend over a long period due to the range of tree ages. In turn, a longer regeneration period and a new stand with an even greater range of ages results. If this process continues over several generations, an all-aged stand is established.
Fire Ecology:
Wildfire is recognized as a natural disturbance that influenced the structure and composition of the climax vegetation of this woodland site. Periodic wildfires prevent over-mature aspen stands and maintain a naturally stratified mosaic of even-aged aspen stands in various stages of successional development. Many aspen stands are even-aged because of the rapid reproduction by suckering after a major disturbance such as fire which removes top-growth. In the absence of fire, harvest, or similiar events, aspen stands becomes uneven-aged. Uneven-aged stands form under stable conditions where the overstory gradually disintegrates with disease or age, and release of suckers occurs.
Quaking aspen has adapted to fire in the following ways.
1.The thin bark has little heat resistance, and quaking aspen is easily top-killed by fire.
2.Root systems of top-killed stems send up a profusion of sprouts for several years after fire.
3.Sprouts grow rapidly by extracting water, nutrients, and photosynthate from an extant root system, and may outcompete other woody vegetation.
4.Following a fire, a new, even-aged quaking aspen stand can develop within a decade.
5.In contrast to most trees, quaking aspen is self-thinning. Without intervention, a mature forest of healthy trees can develop from dense sprouts.
State and transition model
More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective textEcosystem states
State 1 submodel, plant communities
State 1
Reference Plant CommunityCommunity 1.1
Reference Plant Community
This site is composed of one to several quaking aspen clones, with a common genetic makeup and individual phenological and physiological characteristics.
Wildfire is recognized as a natural disturbance that influenced the structure and composition of the climax vegetation of this forest site. Periodic wildfires prevent over-mature aspen stands and maintain a naturally stratified mosaic of even-aged aspen stands in various stages of successional development. Many aspen stands are even-aged because of the rapid reproduction by suckering after a major disturbance such as fire. In the absence of fire, harvest, or similar events, aspen stands become uneven-aged. Uneven-aged stands form under stable conditions where the overstory gradually disintegrates with disease or age, and is replaced by suckers.
An overstory canopy of 25 to 35 percent is assumed to be representative of tree dominance on this site in a pristine environment. Aspen communities are typically multi-layered. Sufficient light is able to penetrate the canopy to support abundant undergrowth
Overstory tree canopy composition is generally 100 percent quaking aspen. Small populations of black cottonwood or narrowleaf cottonwood may sometimes be found intermingled with the aspen overstory. Sapling quaking aspen, willow, and Woods rose are the principal understory shrubs. Slender and streambank wheatgrasses, Nevada bluegrass, sedges, clover, yarrow, and groundsel are other important understory plants associated with this site.
Forest overstory.The visual aspect and vegetal structure are dominated by single-story, quaking aspen that have reached, or are near, maximal heights for the site. Growth of aspen continues during this stage. Diameter growth shows recovery with the release of competition previously endured during the immature forest stage. Tree heights range from 50 to over 80 feet, depending upon site and clonal genotype. Trees have developed tall, straight, clear stems with short, narrow, dome-like crowns. Tree canopy cover ranges from 25 to 40 percent. Understory vegetation is strongly influenced by tree competition, overstory shading, and duff accumulation. Relatively shade tolerant perennial grasses and forbs form a continuous layer beneath tree canopy. Few vegetative shoots and/or saplings of quaking aspen occur in the understory
Forest understory. Understory vegetative composition is about 60 percent grasses, 20 percent forbs and 20 percent shrubs and young trees when the<br /> average overstory canopy is medium (25 to 35 percent). Average understory production ranges from 800 to 1500 pounds per acre with a medium canopy cover. Understory production includes the total annual production of all species within 4 1/2 feet of the ground surface.<br />
Figure 3. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Annual production by plant type
Plant type Low
(lb/acre)Representative value
(lb/acre)High
(lb/acre)Grass/Grasslike 480 720 900 Forb 160 240 300 Shrub/Vine 120 180 225 Tree 40 60 75 Total 800 1200 1500 Additional community tables
Table 6. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Grass/Grasslike1 Primary Perennial Grasses 300–612 slender wheatgrass ELTRT Elymus trachycaulus ssp. trachycaulus 120–288 – sedge CAREX Carex 60–108 – thickspike wheatgrass ELLA3 Elymus lanceolatus 60–108 – 2 Secondary Perennnial Grasses 36–180 Columbia needlegrass ACNEN2 Achnatherum nelsonii ssp. nelsonii 12–60 – mountain brome BRMA4 Bromus marginatus 12–60 – rush JUNCU Juncus 12–60 – Forb3 Perennial Forbs 84–228 ragwort SENEC Senecio 60–108 – clover TRIFO Trifolium 12–60 – yarrow ACHIL Achillea 12–60 – Shrub/Vine4 Primary Shrubs 120–216 Woods' rose ROWO Rosa woodsii 60–108 – willow SALIX Salix 60–108 – 5 Secondary Shrubs 12–60 currant RIBES Ribes 12–60 – Tree6 Trees 60–108 Interpretations
Animal community
Wildlife Interpretations:
Quaking aspen forests provide important breeding, foraging, and resting habitat for a variety of birds and mammals. Wildlife and livestock utilization of quaking aspen communities varies with species composition
of the understory and relative age of the quaking aspen stand. Young stands generally provide the most browse. Quaking aspen crowns can grow out of reach of large ungulates in 6 to 8 years. Although many animals browse quaking aspen year-round, it is especially valuable during fall and winter, when protein levels are high relative to other
browse species.
Livestock Interpretations:
This site is suited to cattle and sheep grazing during the summer and early fall. Livestock use quaking aspen communities for forage and shade. Cattle select for understory grasses while sheep tend to select for forbs. Browsing has a direct impact on aspen. Through the early sapling stage, browsing reduces aspen growth, vigor and numbers. Heavy browsing by sheep or deer can eliminate aspen sucker regeneration. Suckers can be drastically reduced or eliminated by big game browsing on winter ranges. Sheep browse the aspen with increasing pressure through late summer and early fall. Browsing is incidental to grazing by cattle. If cattle grazing is light to moderate, the impact on aspen will also be slight. This relationship, however, is less true for sheep and wild ungulates. Aspen saplings need to attain a minimum height of 55 to 60 inches to avoid destructive browsing by livestock. Harvesting trees under a sound management program for fuelwood, posts or other products, can open up the tree canopy to allow increased production of understory species desirable for grazing and browsing.
The forage value rating is not an ecological evaluation of the understory. The forage value rating is a utilitarian rating of the existing understory plants for use by specific kinds of grazing animals.
Stocking rates vary over time depending upon season of use, climate variations, site, and previous and current management goals. A safe starting stocking rate is an estimated stocking rate that is fine tuned by the client by adaptive management through the year and from year to year.
Example: Sample Calculations using Favorable Year production amounts:
500 lbs of available forage/ac x. 25 (Harvest Efficiency) = 125 lbs forage consumed
125 lbs/790 lbs = .16 AUMs/ac or 6.32 ac/AUM
NOTE: 790 lbs/month for one Animal Unit is used as the baseline for maintenance requirements. This equates to 30 lbs/day of air-dry forage (1000 lb cow at 2.6% of body weight). See NRCS National Range and Pasture Handbook.
Hydrological functions
Mountain slopes covered by quaking aspen provide high yields of good-quality water. Quaking aspen intercepts less snow than conifers, so snowpack is often greater under quaking aspen. Well-stocked quaking aspen stands provide excellent watershed proctection. The trees, the shrub and herbaceous understories, and the litter of quaking aspen stands provide nearly 100 percent soil cover.
Recreational uses
Aesthetic value is derived from the rich hues and textures of the aspen trees, particularly in the fall. The diverse flora and fauna, and the colorful wildflowers in the summer enhance the beauty of this site. The site offers rewarding opportunities to photographers and for nature study. It has high value for hunting, camping, picnicking, cross country skiing and family wood gathering. Management of the aspen woodland should include small, irregularly shaped clearcuts that blend into the natural landscape. Harvesting plans should include a mix of even-aged aspen patches in all size classes. Aspen fits well into management for dispersed recreation activities, but does not tolerate concentrated use, as found in established campgrounds. Encouraging concentrated recreation or developing campgrounds within aspen stands can lead to serious damage, including carving on trees, vandalism, destruction or removal of young suckers and trampling and disturbance of the soil.
Wood products
Historically quaking aspen has been used for mine props, posts, bridge planking, flooring, furniture and fuelwood. This tree has a considerable potential for increased utilization. It makes excellent pulp, excelsior, door corestock, paper,
particleboard, matchsticks, structural flakeboard, lumber products and boxwood. An Quaking aspen pellets are used for fuel.
MANAGEMENT GUIDES AND INTERPRETATIONS
1. LIMITATIONS AND CONSIDERATIONS
a. Potential for sheet and rill erosion is low to moderate depending on slope.
b. Moderate to severe equipment limitations on sites having a high water table.
c. Proper spacing is the key to a well managed, multiple use and multi-product aspen woodland.
d. To begin short-rotation management, older stands with larger trees need to be harvested.
e. Cut residual unmerchantable trees to stim-ulate maximum sucker regeneration and rapid development of a replacement stand-thin resulting sucker stands.
f. Soil compaction and erosion hazards are greatest if logging is done with heavy equipment when soils are saturated. Logging at this time is most damaging to aspen roots, which can reduce suckering. Root carbohydrate reserves are lowest in the spring and harvesting at this time can further reduce sprouting.
2. ESSENTIAL REQUIREMENTS
a. Adequately protect from high intensity wildfire.
b. Protect soils from accelerated erosion.
c. Apply proper grazing management.
3. SILVICULTURAL PRACTICES
a. Harvest cutting - Selectively harvest surplus trees to achieve desired spacing. Harvest stands in small blocks of 1/5 to 1/2 acre with slash left in place to shelter emerging aspen suckers from browsing.
1)Clear-cutting - Clear-cutting is appro-priate when the primary management objective is sustained production of forest products, either saw timber or fiber. Cutting sub-merchantable stems along with the merchantable ones will maximize sucker production, will minimize the presence of diseased or defective growing stock in the new stand, and will avoid suppression of the new crop by residual overstory stems.
2)Partial cutting - Partial cutting may be feasible in some uneven-aged stands where management objectives require vertical canopy diversity or retention of some overstory; partial cutting may result in enough sprouting to adequately regenerate stands. Individual tree or group selection cutting methods can be applied. Extreme care is necessary to avoid injury to residual stems during logging. Partial cutting is not worthwhile in deteriorated aspen clones where root system die-back has reduced suckering.
3)Selective Tree Removal - Remove selected trees on suitable sites to enhance forage production and manage site reproduction.
b. Thinning - Ordinarily, only stands on saw timber sites should be thinned. Pre-commercial thinning may be uneconomical. The low productivity of this site would not justify thinning costs.
c. Protection from disease - There are no proven forest stand treatments that successfully prevent or control disease in aspen. Maintenance of well-stocked stands, minimizing wounding of stems and control damaging agents, and harvesting at the proper rotation age are the best management recommendations that can be made today.
d. Protection from insects - Direct control of insects in aspen forests has not been practical. The environmental side-effects from chemical pesticide spraying usually has not been acceptable in the aspen ecosystem. Maintenance of a well-stocked stand and protection from wounding is the most practical method of coping with insects in the aspen forest.
e. Protection from mammals - Domestic livestock, wild ungulates, porcupines, rodents and hares utilize aspen as food and can have measurable impacts on some stands. Most animal damage can be prevented by careful husbandry of domestic livestock and by population control of wild game. Because most aspen stands are grazed by cattle and/or sheep and have a significant population of wild ungulates, grazing management and game management are important to aspen communities.
f. Fire management - Fire is a natural feature of the aspen ecosystem. Fire is considered responsible for the abundance of aspen in the west, and for the even-aged structure of many stands. Without human intervention, fire appears to be necessary for the continued well-being of aspen on sites where natural degeneration of the clone occurs, or where insects or pests are especially harmful to the stand. Aspen forests do not readily burn. Fires in aspen generally are infrequent, spread slowly, are of low intensity, and are easy to control. In most areas, the conditions suitable for a fire are infrequent in aspen stands. Although aspen forests do not burn readily, aspen trees are extremely sensitive to fire. Even very light fires will kill aspen, because the bark is thin and green, and lacks protective corky layers. Even with adequate fuels, the flammability of adjacent grasslands may make prescribed burning risky. However, where fire can be used with reasonable safety, it is an inexpensive and effective way to naturally regenerate the aspen forest. Moderate intensity fire that kills most or all the overstory will stimulate adequate suckering and will have the least effect on subsequent sucker growth. If fire occurs at infrequent intervals and is moderately intense to kill most or all of the aspen overstory, most aspen sites will remain viable. Frequent fires may adversely affect site quality.
Other information
An undesirable characteristic of quaking aspen stands is their heavy drain on available water in the soil.
Table 7. Representative site productivity
Common name Symbol Site index low Site index high CMAI low CMAI high Age of CMAI Site index curve code Site index curve basis Citation quaking aspen POTR5 50 75 20 28 – – – Supporting information
Type locality
Location 1: Mono County, CA Latitude 38° 21′ 56″ Longitude 119° 32′ 9″ General legal description Toiyabe National Forest. Other references
Airola, D. A. 1980. Northeast Interior Zone: Vol. III - Birds & Vol. IV - Mammals. U.S. Gov. Printing Off.: 1980-690-082/26.
Baker, F. S. 1925. Aspen in the central Rocky Mountain region. USDA, Bulletin 1291, 47 p. Washington D.C.
DeByle, N. V., and R.P. Winokur, editors. Aspen: Ecology and Management in the Western United States. General Technical Report RM-119, Rocky Mtn For & Rng Exp Sta, FS, USDA.
DeByle, N.V., P.J. Urness, and D.L. Blank. 1989. Forage Quality in Burned and Un-burned Aspen Communities. Research Paper INT-404. Inter. Res. Sta., FS, USDA.
Fire Effects Information System[Online], http://www.fs.fed.us/database/feis
Plants Database [Online], http://www.plants.usda.gov
Contributors
ALM
Rangeland health reference sheet
Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.
Author(s)/participant(s) Contact for lead author Date Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
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Number and extent of rills:
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Presence of water flow patterns:
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Number and height of erosional pedestals or terracettes:
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Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
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Number of gullies and erosion associated with gullies:
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Extent of wind scoured, blowouts and/or depositional areas:
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Amount of litter movement (describe size and distance expected to travel):
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Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
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Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
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Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
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Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
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Functional/Structural Groups (list in order of descending dominance by above-ground annual-production or live foliar cover using symbols: >>, >, = to indicate much greater than, greater than, and equal to):
Dominant:
Sub-dominant:
Other:
Additional:
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Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
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Average percent litter cover (%) and depth ( in):
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Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
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Potential invasive (including noxious) species (native and non-native). List species which BOTH characterize degraded states and have the potential to become a dominant or co-dominant species on the ecological site if their future establishment and growth is not actively controlled by management interventions. Species that become dominant for only one to several years (e.g., short-term response to drought or wildfire) are not invasive plants. Note that unlike other indicators, we are describing what is NOT expected in the reference state for the ecological site:
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Perennial plant reproductive capability:
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