Natural Resources
Conservation Service
Ecological site R058AC616MT
Thin Breaks (TB) RRU 58A-C 11-14" p.z.
Last updated: 6/14/2023
Accessed: 11/21/2024
General information
Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site.
Associated sites
| R058AC049MT |
Silty-Steep (SiStp) RRU 58A-C 11-14" p.z. (combined R058AC046MT, R058AC047MT & R058AC048MT into this site) |
|---|---|
| R058AC057MT |
Shallow (Sw) RRU 58A-C 11-14" p.z. |
| R058AC058MT |
Very Shallow (VSw) RRU 58A-C 11-14" p.z. |
Table 1. Dominant plant species
| Tree |
Not specified |
|---|---|
| Shrub |
Not specified |
| Herbaceous |
Not specified |
Physiographic features
This site is typically a complex of
several ecological sites, primarily Shallow and Very Shallow.
It occurs on steep to very steep slopes, usually in excess of 25 percent. Outcroppings of hard bedrock and soft sedimentary beds are major features. Slope aspect can be any direction and can be significant.
Table 2. Representative physiographic features
| Landforms |
(1)
Escarpment
(2) Bluff (3) Ridge |
|---|---|
| Elevation | 2,250 – 4,500 ft |
| Slope | 25% |
| Water table depth | 60 in |
| Aspect | E, S, W |
Climatic features
Major Land Resource Area (MLRA) 58AC in Montana is considered to have a continental climate characterized by cold winters, hot summers, low humidity, light rainfall, and much sunshine. Extremes in temperature are typical. The climate is the result of this MLRA’s location in the geographic center of North America. There are few natural barriers on the northern Great Plains and the winds move freely across the plains and account for rapid changes in temperature. Seasonal precipitation is often limiting for plant growth. Annual fluctuations in species composition and total production are typical depending on the amount and timing of rainfall.
Temperatures can be very extreme in this part of Montana. Summer daytime temperatures are typically quite warm, generally averaging in the mid to upper 80º’s F for July and August. Summertime temperatures will typically reach in the 100º’s F at some point during the summer, and can reach 90º F any month between May and September. Conversely, winter temperatures can be cold, averaging in the mid teens to mid 20º’s F for December and January. There will typically be several days of below zero temperatures each winter. It is not uncommon for temperatures to reach 30–40º F below zero, or even colder, most any winter.
Spring can be windy throughout this MLRA, with winds averaging over 10 mph about 15 percent of the time. Speeds of 50 mph or stronger can occasionally occur as a weather system crosses this part of Montana.
The majority of the rangeland in MLRA 58AC is within the 11 to 14 inch Mean Annual Precipitation (MAP) range. During an average year, 70 to 75 percent of the annual precipitation falls between April and September, which are the primary growing season months.
Snowfall is not heavy in the area, averaging 28 total inches in the Yellowstone Valley. Heavy snowfall occurs infrequently, usually late in the winter or early spring. Snow cover is typically 1 to 3 inches.
The frost-free (32º F.) season averages about 105 to 145 days each year in the uplands, to nearly 170 days along the Yellowstone River Valley.
For local climate station information, refer to http://www.wcc.nrcs.usda.gov/cgibin/state.pl?state=mt.
Table 3. Representative climatic features
| Frost-free period (average) | 135 days |
|---|---|
| Freeze-free period (average) | 155 days |
| Precipitation total (average) | 14 in |
Influencing water features
Soil features
The soils associated with this ecological site are highly variable. They will range from very shallow to deep, depending on landform and presence of ledges, etc. where pockets of deeper soils can accumulate. More detailed and specific information is available by using the ecological site description for the component of this site being investigated (e.g., Shallow).
Table 4. Representative soil features
| Surface texture |
(1) Gravelly sand (2) Flaggy loam |
|---|---|
| Drainage class | Well drained to excessively drained |
| Soil depth | 10 – 40 in |
| Surface fragment cover <=3" | 15 – 20% |
| Available water capacity (0-40in) |
5 in |
| Soil reaction (1:1 water) (0-40in) |
6.6 – 8.4 |
Ecological dynamics
The following are descriptions of several plant communities that may occupy this site:
State and transition model
More interactive model formats are also available.
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View Interactive Models
Click on state and transition labels to scroll to the respective text
State 1 submodel, plant communities
State 2 submodel, plant communities
State 3 submodel, plant communities
State 4 submodel, plant communities
State 1
Plant Community 1: Tall and Medium Grasses/ Forbs, Shrubs
Community 1.1
Plant Community 1: Tall and Medium Grasses/ Forbs, Shrubs
The physical aspect of this site in Historical Climax is that of mixed grass/ shrub land dominated by cool-season bunch grasses and a mixture of shrubs. Approximately 65-75% of the annual production is from grasses and sedges, 5-10% from forbs, and 15-30% is from trees, shrubs and half-shrubs. Canopy cover of shrubs is typically 10 to 35%. Ponderosa pine may occur on this site. The following are descriptions of several plant communities that may occupy this site: It contains a high diversity of tall grasses (bluebunch wheatgrass, prairie sandreed, Indian ricegrass, and green needlegrass), short grasses and sedges (threadleaf sedge, prairie junegrass, plains reedgrass, and sand dropseed), and shrubs (skunkbush sumac, winterfat, Wyoming big sagebrush, and Rocky Mountain juniper). There are also abundant forbs, and half-shrubs which occur in small percentages. Ponderosa pine or limber pine trees are often a component of this plant community.
Figure 1. 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 | 400 | 480 | 570 |
| Shrub/Vine | 130 | 160 | 180 |
| Forb | 40 | 50 | 60 |
| Total | 570 | 690 | 810 |
Table 6. Ground cover
| Tree foliar cover | 0-10% |
|---|---|
| Shrub/vine/liana foliar cover | 5-20% |
| Grass/grasslike foliar cover | 20-50% |
| Forb foliar cover | 5-10% |
| Non-vascular plants | 0% |
| Biological crusts | 0-1% |
| Litter | 0% |
| Surface fragments >0.25" and <=3" | 0% |
| Surface fragments >3" | 0% |
| Bedrock | 0% |
| Water | 0% |
| Bare ground | 0% |
Table 7. Soil surface cover
| Tree basal cover | 0-1% |
|---|---|
| Shrub/vine/liana basal cover | 1-10% |
| Grass/grasslike basal cover | 3-12% |
| Forb basal cover | 1-4% |
| Non-vascular plants | 0% |
| Biological crusts | 1-3% |
| Litter | 30-60% |
| Surface fragments >0.25" and <=3" | 15-20% |
| Surface fragments >3" | 0% |
| Bedrock | 0% |
| Water | 0% |
| Bare ground | 30-60% |
Table 8. Canopy structure (% cover)
| Height Above Ground (ft) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.5 | – | – | – | 5-10% |
| >0.5 <= 1 | – | – | – | – |
| >1 <= 2 | – | 5-20% | 20-50% | – |
| >2 <= 4.5 | – | – | – | – |
| >4.5 <= 13 | – | – | – | – |
| >13 <= 40 | 0-10% | – | – | – |
| >40 <= 80 | – | – | – | – |
| >80 <= 120 | – | – | – | – |
| >120 | – | – | – | – |
State 2
Plant Community 2: Medium and Short Grasses/ Forbs/ Shrubs and Half-Shrubs
Community 2.1
Plant Community 2: Medium and Short Grasses/ Forbs/ Shrubs and Half-Shrubs
Slight disturbances and degradation to the HCPC will result in a plant community dominated by needleandthread, western or thickspike wheatgrass, threadleaf sedge, prairie junegrass, blue grama, various forbs, Wyoming big sagebrush and fringed sagewort. The tall, more palatable grasses (bluebunch wheatgrass, Indian ricegrass, green needlegrass, prairie sandreed) will be present in smaller percentages. The tree component, if present, may also increase. Grass biomass production and litter become reduced on the site as the taller grasses disappear, increasing evaporation and reducing moisture retention. Additional open space in the community can result in undesirable invader species. This plant community provides for moderate soil stability.
State 3
Plant Community 3: Shrubs/ Short Grasses/ Annual Grasses/ Invasive Forbs
Community 3.1
Plant Community 3: Shrubs/ Short Grasses/ Annual Grasses/ Invasive Forbs
With continued heavy disturbance the site will become dominated by shrubs such as big or silver sagebrush, fringed sagewort, rubber rabbitbrush, and Rocky Mountain juniper. Short grasses and sedges increase, such as threadleaf sedge, prairie junegrass, sand dropseed, and blue grama. Needleandthread and western or thickspike wheatgrass will still be present in small amounts. Palatable shrubs and forbs will be mostly absent. Red threeawn, annual grasses (cheatgrass and Japanese brome), invasive forbs such as curlycup gumweed, and broom snakeweed begin to invade the site. This plant community is less productive than Plant Community 1 or 2 (< 200 pounds per acre). The lack of litter and short plant heights result in higher soil temperatures, poor water infiltration rates, and high evapotranspiration, which gives short sod grasses and annuals a competitive advantage over the cool season tall and medium grasses. This community has lost many of the attributes of a healthy rangeland, including good infiltration, minimal erosion and runoff, nutrient cycling and energy flow. There are severe limitations to using seeding and/or mechanical treatment on this site because of the very steep slopes, preponderance of shallow and very shallow soils, and amount of rock outcrop.
State 4
Plant Community 4: Shrubs/ Invader and Annual Grasses/ Short Grasses
Community 4.1
Plant Community 4: Shrubs/ Invader and Annual Grasses/ Short Grasses
With continual heavy disturbance over several years the community will change to one dominated primarily by big or silver sagebrush, fringed sagewort, rubber rabbitbrush, and Rocky Mountain juniper, red threeawn, fringed sagewort, annual grasses, invasive forbs, broom snakeweed and plains pricklypear. This community has extremely reduced productivity of perennial grasses (< 25 pounds per acre). Significant economic inputs and time would be required to move this plant community toward a higher successional stage and a more productive plant community.
Additional community tables
Table 9. Community 1.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | Native grasses | 370–527 | ||||
| bluebunch wheatgrass | PSSP6 | Pseudoroegneria spicata | 171–567 | – | ||
| tufted wheatgrass | ELMA7 | Elymus macrourus | 85–202 | – | ||
| western wheatgrass | PASM | Pascopyrum smithii | 85–202 | – | ||
| prairie sandreed | CALO | Calamovilfa longifolia | 0–122 | – | ||
| needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 28–81 | – | ||
| plains muhly | MUCU3 | Muhlenbergia cuspidata | 0–81 | – | ||
| green needlegrass | NAVI4 | Nassella viridula | 0–40 | – | ||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–40 | – | ||
| 2 | Native grasses and sedges | 0–81 | ||||
| Grass, perennial | 2GP | Grass, perennial | 0–40 | – | ||
| blue grama | BOGR2 | Bouteloua gracilis | 0–40 | – | ||
| needleleaf sedge | CADU6 | Carex duriuscula | 0–40 | – | ||
| threadleaf sedge | CAFI | Carex filifolia | 0–40 | – | ||
| plains reedgrass | CAMO | Calamagrostis montanensis | 0–40 | – | ||
| prairie Junegrass | KOMA | Koeleria macrantha | 0–40 | – | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–40 | – | ||
| 3 | Native grasses | 0–1 | ||||
| Sandberg bluegrass | POSE | Poa secunda | 0–1 | – | ||
| 4 | Native grasses | 0–1 | ||||
| Fendler threeawn | ARPUL | Aristida purpurea var. longiseta | 0–1 | – | ||
| squirreltail | ELEL5 | Elymus elymoides | 0–1 | – | ||
|
Forb
|
||||||
| 5 | Native forbs | 28–81 | ||||
| Forb, perennial | 2FP | Forb, perennial | 0–40 | – | ||
| common yarrow | ACMI2 | Achillea millefolium | 0–40 | – | ||
| tarragon | ARDR4 | Artemisia dracunculus | 0–40 | – | ||
| bastard toadflax | COUM | Comandra umbellata | 0–40 | – | ||
| miner's candle | CRVI4 | Cryptantha virgata | 0–40 | – | ||
| white prairie clover | DACA7 | Dalea candida | 0–40 | – | ||
| purple prairie clover | DAPU5 | Dalea purpurea | 0–40 | – | ||
| buckwheat | ERIOG | Eriogonum | 0–40 | – | ||
| dotted blazing star | LIPU | Liatris punctata | 0–40 | – | ||
| desertparsley | LOMAT | Lomatium | 0–40 | – | ||
| rush skeletonplant | LYJU | Lygodesmia juncea | 0–40 | – | ||
| beardtongue | PENST | Penstemon | 0–40 | – | ||
| spiny phlox | PHHO | Phlox hoodii | 0–40 | – | ||
| scurfpea | PSORA2 | Psoralidium | 0–40 | – | ||
| Missouri goldenrod | SOMI2 | Solidago missouriensis | 0–40 | – | ||
| scarlet globemallow | SPCO | Sphaeralcea coccinea | 0–40 | – | ||
| American vetch | VIAM | Vicia americana | 0–40 | – | ||
| 6 | Native forbs | 1–2 | ||||
| curlycup gumweed | GRSQS2 | Grindelia squarrosa var. squarrosa | 1–2 | – | ||
|
Shrub/Vine
|
||||||
| 7 | Native shrubs, half-shrubs and trees | 85–243 | ||||
| skunkbush sumac | RHTR | Rhus trilobata | 28–202 | – | ||
| soapweed yucca | YUGL | Yucca glauca | 28–81 | – | ||
| Shrub, broadleaf | 2SB | Shrub, broadleaf | 28–81 | – | ||
| silver sagebrush | ARCA13 | Artemisia cana | 28–81 | – | ||
| prairie sagewort | ARFR4 | Artemisia frigida | 28–81 | – | ||
| Wyoming big sagebrush | ARTRW8 | Artemisia tridentata ssp. wyomingensis | 28–81 | – | ||
| shadscale saltbush | ATCO | Atriplex confertifolia | 28–81 | – | ||
| Nuttall's saltbush | ATNU2 | Atriplex nuttallii | 28–81 | – | ||
| rubber rabbitbrush | ERNAN5 | Ericameria nauseosa ssp. nauseosa var. nauseosa | 28–81 | – | ||
| creeping juniper | JUHO2 | Juniperus horizontalis | 28–81 | – | ||
| Rocky Mountain juniper | JUSC2 | Juniperus scopulorum | 28–81 | – | ||
| winterfat | KRLA2 | Krascheninnikovia lanata | 28–81 | – | ||
| limber pine | PIFL2 | Pinus flexilis | 28–81 | – | ||
| ponderosa pine | PIPO | Pinus ponderosa | 28–81 | – | ||
| 8 | Native shrubs and half-shrubs | 0–1 | ||||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–1 | – | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–1 | – | ||
Interpretations
Animal community
Livestock Grazing Interpretations:
Managed livestock grazing is suitable on this site as it has the potential to produce a limited amount of high quality forage. Forage production is limited by steep slopes and shallow soils, and the potential for runoff, which reduces the effectiveness of the precipitation received for plant growth. The steeper slopes and rock outcrop also limit livestock travel and result in poor grazing distribution, especially in areas away from water. Management objectives should include maintenance or improvement of the plant community. Shorter grazing periods and adequate re-growth after grazing are recommended for plant maintenance and recovery. Heavy stocking and season long use of this site can be detrimental and will alter the plant community composition and production over time.
Whenever Plant Community 2 (medium and short grasses) occurs, grazing management strategies need to be implemented to avoid further deterioration. This community is still stable, productive, and healthy provided it receives proper management. This community will respond fairly quickly to improved grazing management including increased growing season rest of key forage plants. Grazing management alone can usually move this community back to one more similar to potential if a good seed source of the taller grasses still exists.
Plant Communities 3 and 4 have significantly reduced forage production (< 150 lbs./acre). Once this site is occupied by either Plant Community 3 or 4, it will be more difficult to restore it to a community that resembles the potential with grazing management alone. Additional growing season rest is often necessary for re-establishment of the desired species and to restore the stability and health of the site.
The potential for using seeding and/or mechanical treatment to improve site health is not feasible due to steep slopes, shallow soils and the amount of exposed rock outcrop.
Wildlife Interpretations:
The Thin Breaks ecological site, with its complex topography and vegetative structure, provides diverse habitat structure for a variety of wildlife species. Historically, mule deer, pronghorn, a variety of seed-eating small mammals and raptors were probably the most conspicuous wildlife species, as they still are. The general area provides thermal and escape cover for big game animals as well as a variety of other wildlife species. Shrub availability on steep, south slopes often provides important winter range for mule deer and elk. Abundant prey and perch sites (on rock outcrops and scattered trees) attract a variety of raptors. The steep, rocky topography provides habitat for interesting songbird species such as rock wrens, canyon wrens and white-throated swifts. Golden eagles and prairie falcons commonly hunt small mammals within this site. Scattered junipers and pines host field sparrows and chipping sparrows. The interface of sandy and shale geologic substrates often results in seeps forming on side-hills and toe slopes. These are an important water source for wildlife as well as a source of biodiversity.
Plant Community 1: Tall and Medium Grasses/ Forbs/ Shrubs (HCPC):
The diversity of forbs, half-shrubs and shrubs provides feeding substrate for a variety of pollinating insects, which are prey for many birds, reptiles and small mammals. Springs and seeps are habitat for amphibians such as tiger salamanders. The short-horned lizard is a representative reptile. The diversity of plant species and life forms, in combination with topographic variation, provides high quality bird habitat. Lark sparrows, green-tailed towhees, mountain bluebirds and golden eagles are examples of birds using this community. Sharp-tailed grouse and sage grouse may use this community for lek sites on ridge tops and fairly level topography. The diversity of forbs and shrubs favors browsers and selective feeders such as mule deer and pronghorn. Large animal nutrition levels are relatively high yearlong because of plant species and life form diversity. Winter range value is often high for big game species when topographic diversity provides south exposures and browse plants such as skunkbush sumac and winterfat are available. Small mammal diversity may be fairly high. Example species include the kangaroo rat, deer mouse, olive-backed pocket mouse and desert cottontail.
Plant Community 2: Medium & Short Grasses/ Forbs/ Shrubs & Half-Shrubs:
Insect diversity may decline with a partial loss of forb variety. The reduction of taller grasses and some desirable shrubs degrades habitat value for many birds, small mammals and big game. Potential increases in half-shrubs and shrubs may maintain big game winter range feeding value, although thermal cover is reduced. Small mammal species diversity declines with the reduction of vegetative diversity and litter cover.
Plant Community 3: Shrubs/ Short Grasses/ Annual Grasses/ Invasive Forbs:
Insects may be abundant at the height of population cycles but species diversity is reduced significantly. Springs and seeps are very degraded which results in poor amphibian habitat. Sparse vegetation and increased bare ground may provide suitable habitat for a few species (i.e. horned larks) but the lack of complex vegetative structure and residual cover makes this community poor habitat in general for most ground-nesting birds and relatively poor big game habitat. Pronghorn and mule deer may forage in this type throughout the year. However, nutritional levels for big game are greatly reduced and are available for a much shorter period as compared to the HCPC.
Plant Community 4: Shrubs/ Invader and Annual Grasses/ Short Grasses:
General wildlife habitat value is very poor in this community. Insect diversity and abundance is considerably reduced which decreases feeding opportunity for amphibians, birds and some small mammals. The lack of complex vegetative structural diversity, a shortened period of active plant growth and loss of ground cover make the habitat inhospitable for many birds and most small mammals. Wyoming big sagebrush and fringed sagewort provide some valuable big game winter forage, w here present. Thermal cover values are very limited with the loss of skunkbush sumac and other shrubs as well as herbaceous cover. Small mammal diversity is very low. The seed-eating deer mouse may be fairly well represented.
Hydrological functions
The soils associated with this ecological site are generally in Hydrologic Soil Group D. The infiltration rates for these soils are variable, depending on surface texture. The runoff potential for this site is high to very high, depending on slope and ground cover/health. Runoff curve numbers generally range from 85 to 94.
Other information
The following is an example of how to calculate the recommended stocking rate. This example does not use production estimates from this specific ecological site. You will need to adjust the annual production values and run the calculations using total annual production values from the ecological sites encountered on each individual ranch/pasture. Before making specific recommendations, an on-site evaluation must be made.
Example of total annual production amounts by type of year:
Favorable years = 2200 lbs/acre
Normal years = 1480 lbs/acre
Unfavorable years = 1200 lbs/acre
It is recommended that on slopes of 30% or less, stocking rate should be derived from the total annual production pounds minus 500 pounds for residual dry matter and 25% harvest efficiency. On slopes over 30%, stocking rate is derived from total annual production pounds minus 800 pounds for residual dry matter and 25% harvest efficiency. Refer to the NRCS National Range and Pasture Handbook for a list of Animal Unit Equivalents.
Sample Calculations using Favorable Year production amounts:
< 30% slopes: AUM/AC = [(2200-500)(0.25)]/915 lbs/month for one AU = 0.46 AUM/AC
AC/AUM = (1.0 AU)/(0.46AUM/AC) = 2.2 AC/AUM
> 30% slopes: AUM/AC = [(2200-800)(0.25)]/915 lbs/month for one AU = 0.38 AUM/AC
AC/AUM = (1.0 AU)/(0.38 AUM/AC) = 2.6 AC/AUM
NOTE: 915 lbs/month for one Animal Unit is used as the baseline for maintenance requirements. This equates to 30 lbs/day of air-dry forage (1200 lb cow at 2.5% of body weight).
Supporting information
Inventory data references
NRCS-Production & Composition Record for Native Grazing Lands (Range-417): 2
BLM-Soil & Vegetation Inventory Method (SVIM) Data: 8
NRCS-Range Condition Record (ECS-2): 2
NRCS-Range/Soil Correlation Observations & Soil 232 notes: 5
Other references
Field Offices where this site occurs within the state:
Big Sandy
Big Timber
Billings
Chinook
Columbus
Crow Agency
Fort Belknap
Hardin
Harlowton
Joliet
Lewistown
Malta
Roundup
Stanford
White Sulphur Springs
Winnett
Contributors
MJR, REL, RSN, POH
RSN
Approval
Kirt Walstad, 6/14/2023
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) | Loretta Metz |
|---|---|
| Contact for lead author | |
| Date | 04/23/2005 |
| Approved by | Kirt Walstad |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
Because all slopes on this site exceed 25% and bare ground is 30-60%, rills are present. They are generally < 3.0 inches deep, < 4.0 inches wide, and < 20.0 feet long. -
Presence of water flow patterns:
Will generally be rare on this site, but with the steeper slopes (>35%), and 15-30% bare ground, there may be areas which show accumulations of litter due to water movement, especially after severe storms. -
Number and height of erosional pedestals or terracettes:
Wind and water erosion occurs, and there may be some plants with pedestals up to 0.5 inches in height. Terracettes are generally not present, but where they do occur, they are a natural geological feature. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
Bare ground is between 30-60%. -
Number of gullies and erosion associated with gullies:
Gully erosion is possible, but has not been quantified for this site. -
Extent of wind scoured, blowouts and/or depositional areas:
Wind scoured areas are uncommon, but may be evident. -
Amount of litter movement (describe size and distance expected to travel):
Litter movement will be minimal on the gradual slopes, however on the steeper slopes there will be evidence of litter movement (i.e. debris dams) which may travel greater than 10 feet on steeper slopes. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Stability values of 2-3 in plant interspaces. Stability values of 3-4 under plant canopies and at plant bases. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Organic matter in the A-horizon is between 0.5–1.5%. A-horizon is 1-2 inches thick. Surface structure should be moderate or strong granular to subangular blocky. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Bunchgrasses and shrubs/trees dominate this site. Perennial herbaceous plants are spaced 2-4 feet apart. Shrub species are spaced 4-16 feet apart. Trees are sparse. Areas of bare soil will have a higher potential for runoff and poorer infiltration rates. Larger areas with exposed rock will increase runoff on this site and may induce erosion below those areas. -
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
None. -
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:
cool season, mid-height, native perennial bunchgrasses >> native shrubs > warm season, short-height perennial grasses > native perennial and annual forbs.Sub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Plant mortality is low; decadence is minimal except in prolonged periods of drought. -
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
570 – 810 #/acre. -
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:
big sagebrush, silver sagebrush, rubber rabbitbrush, Rocky Mountain juniper, threadleaf sedge, blue grama, broom snakeweed, fringed sagewort, plains pricklypear, cheatgrass, Japanese brome, red threeawn. -
Perennial plant reproductive capability:
All species are capable of reproducing.
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