Natural Resources
Conservation Service
Ecological site R035XY263UT
Semidesert Very Steep Stony Loam (Two-Needle Pinyon, Utah Juniper)
Accessed: 06/02/2024
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.
Figure 1. Mapped extent
Areas shown in blue indicate the maximum mapped extent of this ecological site. Other ecological sites likely occur within the highlighted areas. It is also possible for this ecological site to occur outside of highlighted areas if detailed soil survey has not been completed or recently updated.
MLRA notes
Major Land Resource Area (MLRA): 035X–Colorado Plateau
This ecological site occurs in the northern portion of MLRA 35, Colorado Plateau Province. It is found principally in the Canyon Lands and High Plateaus of Utah sections within that MLRA. This area has been stucturally uplifted over time while rivers flowing across it were cutting down into its bedrock. Areas of shale, sandstone, limestone, dolomite, and volcanic rock outcrop are found throughout the region.
Associated sites
| R035XY240UT |
Semidesert Steep Shallow Loam (Utah Juniper-Two-Needle Pinyon) |
|---|---|
| R035XY260UT |
Semidesert Very Steep Stony Loam (Salina Wildrye) |
Similar sites
| R035XY146UT |
Desert Very Steep Stony Loam (Shadscale) |
|---|---|
| R035XY260UT |
Semidesert Very Steep Stony Loam (Salina Wildrye) |
Table 1. Dominant plant species
| Tree |
(1) Pinus edulis |
|---|---|
| Shrub |
(1) Artemisia bigelovii |
| Herbaceous |
(1) Achnatherum hymenoides |
Physiographic features
This site occurs on canyon sideslopes, talus slopes, mountain sides, and steep alluvial fans. Runoff potential is high to very high due the sites shallow soils and steep slopes. Slopes typically range from 30-70%. Elevations generally range from 4100-6800 ft.
Table 2. Representative physiographic features
| Landforms |
(1)
Mountain slope
(2) Valley side (3) Alluvial fan |
|---|---|
| Flooding frequency | None |
| Ponding frequency | None |
| Elevation | 4,100 – 6,800 ft |
| Slope | 30 – 70% |
| Aspect | Aspect is not a significant factor |
Climatic features
The climate is characterized by hot summers and cool to warm winters which can be slightly modified by local topographic conditions such as aspect. Large fluctuations in daily temperatures are common. Mean annual air temperatures range from 46-59 degrees Fahrenheit. Average annual precipitation is 8 to 11 inches. Approximately 75 percent occurs as rain from March through October. On the average, February, June, and December are the driest months and May, August, September, and October are the wettest months. Precipitation is extremely variable from month to month and from year to year. Much of the summer precipitation occurs as convection thunderstorms.
Table 3. Representative climatic features
| Frost-free period (average) | 181 days |
|---|---|
| Freeze-free period (average) | 216 days |
| Precipitation total (average) | 11 in |
Figure 2. Monthly precipitation range
Figure 3. Monthly average minimum and maximum temperature
Influencing water features
There are no water features influencing this site.
Soil features
Characteristic soils in this site are moderately deep to deep and somewhat excessively well drained. The soil moisture and temperature regimes are ustic aridic and mesic respectively. Typically, the dry surface color is reddish or brown. These soils formed in alluvium, colluvium and residuum deposits derived mainly from sandstone parent material. Soil textures range from very channery loams to very stony loamy fine sands. They are slightly saline and slightly to moderately alkaline. Available water capacity is 0.4 to 3.1 inches.
This site has been used in the following soil surveys and has been correlated to the following components:
UT641 – Washington County Area – Mathis
UT646 – Dixie National Forest – Mathis; Reef
UT651 – Fishlake National Forest East Portion – Reef
UT685 – Capital Reef National Park – Reef, Catahoula, Strych, Milok, Ustic Torriorthents;
UT686 – Escalante Grand Staircase National Monument – Reef
UT687 – Arches National Park – Reef
UT688 – Canyonlands National Park – Reef,
Typical Profile:
A1 – 0-4 inches; very stony loamy fine sand; slightly effervescent; slightly alkaline
A2 – 4-10 inches; gravelly loamy fine sand; strongly effervesent; strongly alkaline
C1 – 10-26 inches; very gravelly loamy sand; strongly efferverscent; strongly alkaline
C2 – 10-26 inches; very gravelly fine sand; strongly effervescent; strongly alkaline
R – 33 inches; sandstone bedrock
Table 4. Representative soil features
| Parent material |
(1)
Colluvium
–
sandstone
|
|---|---|
| Surface texture |
(1) Very channery loamy sand (2) Very channery loam (3) Very flaggy fine sandy loam |
| Family particle size |
(1) Loamy |
| Drainage class | Well drained to somewhat excessively drained |
| Permeability class | Moderately rapid to rapid |
| Soil depth | 20 – 79 in |
| Surface fragment cover <=3" | 20 – 50% |
| Surface fragment cover >3" | 20% |
| Available water capacity (0-40in) |
0.4 – 3.1 in |
| Calcium carbonate equivalent (0-40in) |
1 – 20% |
| Electrical conductivity (0-40in) |
4 mmhos/cm |
| Sodium adsorption ratio (0-40in) |
5 |
| Soil reaction (1:1 water) (0-40in) |
7.4 – 8.4 |
| Subsurface fragment volume <=3" (Depth not specified) |
29% |
| Subsurface fragment volume >3" (Depth not specified) |
63% |
Ecological dynamics
This site developed under Colorado Plateau ecological conditions, and the natural influences of herbivory and climate. Species composition is generally dominated by a very sparse layer of two-needle pinyon and Utah juniper. Bigelow sagebrush, mormon tea and blackbrush are common shrub species. Perennial herbaceous species occurrence is highly variable with Indian ricegrass, Salina wildrye and desert needlegrass found most often. There is no evidence to indicate that this site historically maintained a short burn cycle. Until further research indicates that fire played a significant role in the ecosystem processes of this site, this sites State and Transition model will not include fire as a disturbance in the reference state.
Drought and insect damage appear to be the main driving factors in many pinyon/juniper communities. Betancourt et al. (1993), noted that pinyon and juniper woodlands in the southwest appear to be more susceptible to large die-offs during droughts, than at other locations. If a severe drought persists, two-needle pinyon trees, being more susceptible to drought and insect damage than Utah juniper, appear to die out first, while the Utah juniper trees may survive. This event could allow for an increase in shrubs and herbaceous species during periods when wetter years return.
As vegetative communities respond to changes caused by natural occurrences that allow them to cross ecological thresholds, a return to previous states may not be possible without major energy inputs. The amount of energy input needed to affect desired vegetative shifts depends on the present biotic and abiotic features and the desired results.
The following State and Transition diagram depicts the most commonly occurring plant communities found on this ecological site. It does not necessarily depict all the plant communities that can occur, but it does show the most prevalent and repeatable. As more data are collected, some of these plant communities will be revised or removed, and new ones may be added. These plant communities capture the current knowledge and experience at the time of this revision. This model was developed using range data collected in 2006 and 2007 in Arches and Canyonlands National Park in Southeastern Utah. Both ocular and measured data was collected and utilized.
State and transition model
More interactive model formats are also available.
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More interactive model formats are also available.
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Click on state and transition labels to scroll to the respective text
Ecosystem states
State 1 submodel, plant communities
State 2 submodel, plant communities
State 1
Reference State
This Reference State was determined by the study of rangeland relic areas and areas protected from excessive disturbance and influences such as grazing and recreation. Literature review, historical accounts and observations of trends in plant community dynamics under a variety of sites has also been considered. Community phases, community pathways, other states, transitions, and thresholds, have been determined through similar studies and experience. This state represents the natural range of variability that historically dominated the dynamics of this ecological site. This state includes the biotic communities that would have been expressed on the ecological site if all successional sequences were completed without interferences by man under the present environmental conditions; natural disturbances are inherent in its development. This state is dominated by a very sparse canory of two-needle pinyon and Utah juniper with a well developed understory of native shrubs, perennial grasses and perennial and annual forbs. The primary disturbance mechanisms for this site in the reference condition include drought and insects. Reference state: Community phases maintained by drought and insect pathogen cycles. Indicators: A well developed shrub and grass understory co-existing with a canopy of Utah juniper and Two-needle pinyon. Feedbacks: Infrequent, but regular droughts that reduce tree cover. At-risk Community Phase: All communities are at risk when plants in the understory are stressed, and nutrients become available for invasives to establish. Trigger: The introduction of invasive plants into the understory.
Community 1.1
Two-needle pinyon, Utah juniper Shrubland with Perennial Grasses
Figure 4. Pinyon/juniper with perennial grasses
This plant community phase is characterized by a very sparse canopy of two-needle pinyon and Utah juniper, with a well developed shrub layer and perennial grass understory. Shrubs commonly seen include Bigelow’s sagebrush and mormon tea. Typical grasses include Indian ricegrass and Salina wildrye. Forb composition varies greatly depending on seed source, soil, and growing conditions. Other grasses and shrubs are also present; however, species composition varies from one site to the next. Surface rock fragments ranging from gravels to boulders make up the majority of cover on this site and may be has high as 65%. The following tables provide an example of the typical vegetative floristics of a Community Phase 1.1 site.
Figure 5. 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) |
|---|---|---|---|
| Shrub/Vine | 50 | 80 | 120 |
| Grass/Grasslike | 45 | 65 | 95 |
| Tree | 30 | 55 | 75 |
| Forb | 10 | 20 | 30 |
| Total | 135 | 220 | 320 |
Table 6. Ground cover
| Tree foliar cover | 5-10% |
|---|---|
| Shrub/vine/liana foliar cover | 3-15% |
| Grass/grasslike foliar cover | 2-15% |
| Forb foliar cover | 2-10% |
| Non-vascular plants | 0% |
| Biological crusts | 0-15% |
| Litter | 2-5% |
| Surface fragments >0.25" and <=3" | 35-60% |
| Surface fragments >3" | 35-70% |
| Bedrock | 8-33% |
| Water | 0% |
| Bare ground | 5-30% |
Table 7. Canopy structure (% cover)
| Height Above Ground (ft) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.5 | – | 0-5% | 2-8% | 0-5% |
| >0.5 <= 1 | – | 0-5% | 2-10% | 0-5% |
| >1 <= 2 | 0-5% | 3-10% | 2-5% | 0-5% |
| >2 <= 4.5 | 0-5% | 0-5% | – | – |
| >4.5 <= 13 | 5-10% | – | – | – |
| >13 <= 40 | 5-10% | – | – | – |
| >40 <= 80 | – | – | – | – |
| >80 <= 120 | – | – | – | – |
| >120 | – | – | – | – |
Community 1.2
Utah juniper Shrubland with Perennial Grasses
Figure 6. Utah juniper with perennial grasses
This community phase is characterized by a very sparse canopy of Utah juniper. Other commonly occurring plants include Bigelow’s sagebrush mormon tea. Indian ricegrass, and a variety of other perennial grasses and forbs occupy the understory. Two-needle pinyon may be present in small amounts. The sites species composition varies greatly from one location to another depending on seed source, soil, and growing conditions. Surface rock fragments include from channers, gravels to boulders and run as high as 65% cover. The following tables provide an example of the typical vegetative floristics of a Community Phase 1.2 site.
Figure 7. Annual production by plant type (representative values) or group (midpoint values)
Table 8. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Shrub/Vine | 50 | 80 | 110 |
| Grass/Grasslike | 25 | 50 | 80 |
| Tree | 20 | 35 | 50 |
| Forb | 10 | 20 | 25 |
| Total | 105 | 185 | 265 |
Table 9. Ground cover
| Tree foliar cover | 0-10% |
|---|---|
| Shrub/vine/liana foliar cover | 3-19% |
| Grass/grasslike foliar cover | 2-10% |
| Forb foliar cover | 2-9% |
| Non-vascular plants | 0% |
| Biological crusts | 0-24% |
| Litter | 2-5% |
| Surface fragments >0.25" and <=3" | 0-50% |
| Surface fragments >3" | 0-20% |
| Bedrock | 4-20% |
| Water | 0% |
| Bare ground | 8-30% |
Table 10. Canopy structure (% cover)
| Height Above Ground (ft) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.5 | – | 0-5% | 2-8% | 0-5% |
| >0.5 <= 1 | – | 0-5% | 2-10% | 0-5% |
| >1 <= 2 | 0-5% | 3-10% | 2-5% | 0-5% |
| >2 <= 4.5 | 0-5% | 0-5% | – | – |
| >4.5 <= 13 | 5-10% | – | – | – |
| >13 <= 40 | 2-10% | – | – | – |
| >40 <= 80 | – | – | – | – |
| >80 <= 120 | – | – | – | – |
| >120 | – | – | – | – |
Pathway 1.1A
Community 1.1 to 1.2
This pathway occurs as drought and/or insect herbivory removes two-needle pinyon from the site. Drought can also impact shrub and herbaceous production which may be reduced until more normal weather patterns return. A reduction in the overstory canopy may also allow for more nutrients to be captured by perennial grasses and shrubs.
Pathway 1.2A
Community 1.2 to 1.1
This pathway occurs as normal to above average precipitation patterns coupled with time, allow for the reestablishment and persistence of two-needle pinyon and other less drought tolerant shrubs and grasses.
State 2
Current Potential State
This state is very similar to the reference state, except that invasive grasses and/or forbs are present in all phases. The primary disturbance mechanisms for this state include natural and human caused disturbances; however, due to steep slopes there are very little man induced disturbances. Drought and insects may influence the community shifts. Trailing of livestock to water and some minor recreational activities (i.e. hiking) are the most common and have very little impact on the site other than introduction of invasive grasses and forbs. The shift in species composition could affect nutrient cycling, hydrology and soil stability. At this time there is no known way to effectively remove invasive plants from the site once they have become established. Therefore, this site is often irreversibly altered from the reference state Current Potential State: Community phases maintained by drought and insect herbivory cycles. Indicators: A shrub and grass understory co-existing with a canopy of Utah juniper. Feedbacks: Infrequent, but regular droughts to reduce tree cover. Establishment of invasive plant species such as cheatgrass.
Community 2.1
Two-needle pinyon, Utah juniper Shrubland with Invasive Species
Figure 8. Pinyon/juniper with perennial grasses & weeds
This plant community phase is characterized by a very sparse canopy of two-needle pinyon and Utah juniper, with a mixed shrub and perennial grass understory. Shrubs commonly seen include Bigelow’s sagebrush and mormon tea. Grasses that typically inhabit this site include cheatgrass, Indian ricegrass, and Salina wildrye. Forb composition varies greatly depending on seed source, soil, and growing conditions. Other grasses and shrubs are present; however, species composition varies from one site to the next. Surface rock fragments ranging from gravels to boulders make up the majority of cover for this site and may be has high as 65%. The following tables provide an example of the typical vegetative floristics of a Community Phase 2.1 site.
Figure 9. Annual production by plant type (representative values) or group (midpoint values)
Table 11. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Shrub/Vine | 50 | 80 | 120 |
| Grass/Grasslike | 45 | 65 | 95 |
| Tree | 30 | 55 | 75 |
| Forb | 10 | 20 | 30 |
| Total | 135 | 220 | 320 |
Table 12. Ground cover
| Tree foliar cover | 0-10% |
|---|---|
| Shrub/vine/liana foliar cover | 3-16% |
| Grass/grasslike foliar cover | 2-18% |
| Forb foliar cover | 2-9% |
| Non-vascular plants | 0% |
| Biological crusts | 0-13% |
| Litter | 2-5% |
| Surface fragments >0.25" and <=3" | 0-50% |
| Surface fragments >3" | 0-20% |
| Bedrock | 4-20% |
| Water | 0% |
| Bare ground | 8-30% |
Table 13. Canopy structure (% cover)
| Height Above Ground (ft) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.5 | – | 0-5% | 2-8% | 0-5% |
| >0.5 <= 1 | – | 0-5% | 2-10% | 0-5% |
| >1 <= 2 | 0-5% | 3-10% | 2-5% | 0-5% |
| >2 <= 4.5 | 0-5% | 0-5% | – | – |
| >4.5 <= 13 | 5-10% | – | – | – |
| >13 <= 40 | 5-10% | – | – | – |
| >40 <= 80 | – | – | – | – |
| >80 <= 120 | – | – | – | – |
| >120 | – | – | – | – |
Community 2.2
Utah juniper Shrubland with Invasive Species
Figure 10. Utah juniper with perennial grasses & weeds
This plant community phase is characterized by a very sparse canopy of Utah juniper. Other commonly occurring plants include Bigelow’s sagebrush, mormon tea, cheatgrass, Indian ricegrass, and various forbs, including invasive species. Pinyon may be present in small amounts. Forb composition varies greatly depending on seed source, soil, and growing conditions. Other grasses, shrubs, and trees are present,however, species composition varies from one site to the next. Surface rock fragments ranging from gravels to boulders make up the majority of cover for this site and may be has high as 65%. The following tables provide an example of the typical vegetative floristics of a Community Phase 2.2 site.
Figure 11. Annual production by plant type (representative values) or group (midpoint values)
Table 14. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Shrub/Vine | 45 | 80 | 110 |
| Grass/Grasslike | 15 | 50 | 80 |
| Tree | 15 | 35 | 50 |
| Forb | 10 | 20 | 25 |
| Total | 85 | 185 | 265 |
Table 15. Ground cover
| Tree foliar cover | 0-10% |
|---|---|
| Shrub/vine/liana foliar cover | 3-19% |
| Grass/grasslike foliar cover | 0-10% |
| Forb foliar cover | 2-9% |
| Non-vascular plants | 0% |
| Biological crusts | 0-24% |
| Litter | 2-5% |
| Surface fragments >0.25" and <=3" | 0-50% |
| Surface fragments >3" | 0-20% |
| Bedrock | 4-20% |
| Water | 0% |
| Bare ground | 8-30% |
Table 16. Canopy structure (% cover)
| Height Above Ground (ft) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.5 | – | 0-5% | 2-8% | 0-5% |
| >0.5 <= 1 | – | 0-5% | 2-10% | 0-5% |
| >1 <= 2 | 0-5% | 3-10% | 2-5% | 0-5% |
| >2 <= 4.5 | 0-5% | 0-5% | – | – |
| >4.5 <= 13 | 5-10% | – | – | – |
| >13 <= 40 | 5-10% | – | – | – |
| >40 <= 80 | – | – | – | – |
| >80 <= 120 | – | – | – | – |
| >120 | – | – | – | – |
Pathway 2.1A
Community 2.1 to 2.2
This pathway occurs as drought and/or insect herbivory removes two-needle pinyon from the site. Drought can also impact shrub and herbaceous production which may be reduced until more normal weather patterns return. A reduction in the overstory canopy may also allow for more nutrients to be captured by perennial grasses and shrubs. Invasive species may also increase during periods favorable for annual growth.
Pathway 2.2A
Community 2.2 to 2.1
This pathway occurs as normal to above average precipitation patterns coupled with time, allow for the reestablishment and persistence of two-needle pinyon and other less drought tolerant shrubs and grasses. Invasive annual species may also increase during this time.
Transition T1a
State 1 to 2
Transition from Reference State (State 1) to Current Potential State (State 2). This transition from the perennial grass and forb understory found in the reference state to a state that has contains invasive plants. This transition occurs as natural and/or management actions favor an increase in invasive grasses and forbs, especially annuals. Possible events include the mere presence of invasive species seed sources and extended droughts.
Additional community tables
Table 17. Community 1.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Tree
|
||||||
| 1 | Dominant Tree | 30–75 | ||||
| twoneedle pinyon | PIED | Pinus edulis | 8–40 | – | ||
| Utah juniper | JUOS | Juniperus osteosperma | 8–35 | – | ||
|
Shrub/Vine
|
||||||
| 2 | Dominant Shrubs | 10–60 | ||||
| Bigelow sage | ARBI3 | Artemisia bigelovii | 3–60 | – | ||
| mormon tea | EPVI | Ephedra viridis | 0–20 | – | ||
| 3 | Sub-dominant Shrub | 40–60 | ||||
| sumac | RHUS | Rhus | 0–50 | – | ||
| singleleaf ash | FRAN2 | Fraxinus anomala | 0–50 | – | ||
| Utah serviceberry | AMUT | Amelanchier utahensis | 0–40 | – | ||
| blackbrush | CORA | Coleogyne ramosissima | 0–25 | – | ||
| Martin's ceanothus | CEMA2 | Ceanothus martinii | 0–20 | – | ||
| littleleaf mock orange | PHMI4 | Philadelphus microphyllus | 0–20 | – | ||
| brickellbush | BRICK | Brickellia | 0–15 | – | ||
| littleleaf mountain mahogany | CEIN7 | Cercocarpus intricatus | 0–13 | – | ||
| Stansbury cliffrose | PUST | Purshia stansburiana | 0–13 | – | ||
| rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–13 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–13 | – | ||
| roundleaf buffaloberry | SHRO | Shepherdia rotundifolia | 0–12 | – | ||
| crispleaf buckwheat | ERCO14 | Eriogonum corymbosum | 0–10 | – | ||
| spineless horsebrush | TECA2 | Tetradymia canescens | 0–5 | – | ||
| Fremont's mahonia | MAFR3 | Mahonia fremontii | 0–5 | – | ||
| Torrey's jointfir | EPTO | Ephedra torreyana | 0–5 | – | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–3 | – | ||
| yellow rabbitbrush | CHVI8 | Chrysothamnus viscidiflorus | 0–3 | – | ||
| narrowleaf yucca | YUAN2 | Yucca angustissima | 0–3 | – | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–1 | – | ||
| Whipple's fishhook cactus | SCWH | Sclerocactus whipplei | 0–1 | – | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–1 | – | ||
|
Grass/Grasslike
|
||||||
| 3 | Dominant Grass | 45–75 | ||||
| saline wildrye | LESAS | Leymus salinus ssp. salinus | 0–75 | – | ||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 5–75 | – | ||
| James' galleta | PLJA | Pleuraphis jamesii | 5–50 | – | ||
| needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 0–30 | – | ||
| 1 | Sub-dominant Grass | 0–20 | ||||
| slender wheatgrass | ELTR7 | Elymus trachycaulus | 0–20 | – | ||
| bluegrass | POA | Poa | 0–20 | – | ||
| New Mexico feathergrass | HENE5 | Hesperostipa neomexicana | 0–15 | – | ||
| Grass, annual | 2GA | Grass, annual | 0–10 | – | ||
| Grass, perennial | 2GP | Grass, perennial | 0–10 | – | ||
| desert needlegrass | ACSP12 | Achnatherum speciosum | 0–5 | – | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–5 | – | ||
|
Forb
|
||||||
| 2 | Forbs | 10–30 | ||||
| rock goldenrod | PEPU7 | Petradoria pumila | 0–25 | – | ||
| browneyed Susan | RUTR2 | Rudbeckia triloba | 0–13 | – | ||
| desert princesplume | STPI | Stanleya pinnata | 0–13 | – | ||
| Newberry's twinpod | PHNE5 | Physaria newberryi | 0–8 | – | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–8 | – | ||
| lobeleaf groundsel | PAMU11 | Packera multilobata | 0–8 | – | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–5 | – | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–3 | – | ||
| roughseed cryptantha | CRFL6 | Cryptantha flavoculata | 0–3 | – | ||
| larkspur | DELPH | Delphinium | 0–3 | – | ||
| wedgeleaf draba | DRCU | Draba cuneifolia | 0–2 | – | ||
| Wetherill's buckwheat | ERWE | Eriogonum wetherillii | 0–2 | – | ||
| gilia | GILIA | Gilia | 0–2 | – | ||
| pointed gumweed | GRFA | Grindelia fastigiata | 0–2 | – | ||
| beardtongue | PENST | Penstemon | 0–2 | – | ||
| primrose | PRIMU | Primula | 0–2 | – | ||
| thrift mock goldenweed | STAR10 | Stenotus armerioides | 0–2 | – | ||
| longbeak streptanthella | STLO4 | Streptanthella longirostris | 0–2 | – | ||
| woolly locoweed | ASMO7 | Astragalus mollissimus | 0–1 | – | ||
| Wright's bird's beak | COWR2 | Cordylanthus wrightii | 0–1 | – | ||
Table 18. Community 1.2 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Tree
|
||||||
| 1 | Dominant Shrubs | 20–50 | ||||
| Utah juniper | JUOS | Juniperus osteosperma | 20–50 | – | ||
| twoneedle pinyon | PIED | Pinus edulis | 20–5 | – | ||
|
Shrub/Vine
|
||||||
| 2 | Dominant Shrubs | 10–50 | ||||
| Bigelow sage | ARBI3 | Artemisia bigelovii | 0–50 | – | ||
| mormon tea | EPVI | Ephedra viridis | 0–10 | – | ||
| 3 | Sub-dominant Shrubs | 40–60 | ||||
| yellow rabbitbrush | CHVI8 | Chrysothamnus viscidiflorus | 0–42 | – | ||
| Utah serviceberry | AMUT | Amelanchier utahensis | 0–40 | – | ||
| singleleaf ash | FRAN2 | Fraxinus anomala | 0–40 | – | ||
| crispleaf buckwheat | ERCO14 | Eriogonum corymbosum | 0–30 | – | ||
| sumac | RHUS | Rhus | 0–30 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–27 | – | ||
| blackbrush | CORA | Coleogyne ramosissima | 0–24 | – | ||
| littleleaf mock orange | PHMI4 | Philadelphus microphyllus | 0–22 | – | ||
| Martin's ceanothus | CEMA2 | Ceanothus martinii | 0–20 | – | ||
| roundleaf buffaloberry | SHRO | Shepherdia rotundifolia | 0–13 | – | ||
| Stansbury cliffrose | PUST | Purshia stansburiana | 0–13 | – | ||
| rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–13 | – | ||
| littleleaf mountain mahogany | CEIN7 | Cercocarpus intricatus | 0–13 | – | ||
| brickellbush | BRICK | Brickellia | 0–10 | – | ||
| spineless horsebrush | TECA2 | Tetradymia canescens | 0–5 | – | ||
| Fremont's mahonia | MAFR3 | Mahonia fremontii | 0–5 | – | ||
| Torrey's jointfir | EPTO | Ephedra torreyana | 0–4 | – | ||
| narrowleaf yucca | YUAN2 | Yucca angustissima | 0–3 | – | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–1 | – | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–1 | – | ||
|
Grass/Grasslike
|
||||||
| 3 | Grass | 25–60 | ||||
| saline wildrye | LESAS | Leymus salinus ssp. salinus | 0–50 | – | ||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–50 | – | ||
| needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 0–20 | – | ||
| James' galleta | PLJA | Pleuraphis jamesii | 5–20 | – | ||
| 1 | Sub-dominant Grass | 0–20 | ||||
| slender wheatgrass | ELTR7 | Elymus trachycaulus | 0–20 | – | ||
| New Mexico feathergrass | HENE5 | Hesperostipa neomexicana | 0–13 | – | ||
| Grass, annual | 2GA | Grass, annual | 0–10 | – | ||
| Grass, perennial | 2GP | Grass, perennial | 0–10 | – | ||
| desert needlegrass | ACSP12 | Achnatherum speciosum | 0–8 | – | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–5 | – | ||
| bluegrass | POA | Poa | 0–5 | – | ||
|
Forb
|
||||||
| 2 | Forbs | 10–25 | ||||
| lobeleaf groundsel | PAMU11 | Packera multilobata | 0–24 | – | ||
| browneyed Susan | RUTR2 | Rudbeckia triloba | 0–13 | – | ||
| desert princesplume | STPI | Stanleya pinnata | 0–13 | – | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–8 | – | ||
| Newberry's twinpod | PHNE5 | Physaria newberryi | 0–8 | – | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–4 | – | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–3 | – | ||
| roughseed cryptantha | CRFL6 | Cryptantha flavoculata | 0–3 | – | ||
| larkspur | DELPH | Delphinium | 0–2 | – | ||
| Wetherill's buckwheat | ERWE | Eriogonum wetherillii | 0–2 | – | ||
| primrose | PRIMU | Primula | 0–2 | – | ||
| beardtongue | PENST | Penstemon | 0–2 | – | ||
| thrift mock goldenweed | STAR10 | Stenotus armerioides | 0–2 | – | ||
| longbeak streptanthella | STLO4 | Streptanthella longirostris | 0–1 | – | ||
| gilia | GILIA | Gilia | 0–1 | – | ||
| pointed gumweed | GRFA | Grindelia fastigiata | 0–1 | – | ||
| woolly locoweed | ASMO7 | Astragalus mollissimus | 0–1 | – | ||
| Wright's bird's beak | COWR2 | Cordylanthus wrightii | 0–1 | – | ||
Table 19. Community 2.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Tree
|
||||||
| 1 | Dominant Tree | 30–75 | ||||
| twoneedle pinyon | PIED | Pinus edulis | 8–42 | – | ||
| Utah juniper | JUOS | Juniperus osteosperma | 8–33 | – | ||
|
Shrub/Vine
|
||||||
| 2 | Dominant Shrubs | 10–60 | ||||
| Bigelow sage | ARBI3 | Artemisia bigelovii | 3–60 | – | ||
| mormon tea | EPVI | Ephedra viridis | 0–20 | – | ||
| 3 | Sub-dominant Shrubs | 40–60 | ||||
| sumac | RHUS | Rhus | 0–58 | – | ||
| singleleaf ash | FRAN2 | Fraxinus anomala | 0–50 | – | ||
| Utah serviceberry | AMUT | Amelanchier utahensis | 0–42 | – | ||
| blackbrush | CORA | Coleogyne ramosissima | 0–24 | – | ||
| littleleaf mock orange | PHMI4 | Philadelphus microphyllus | 0–22 | – | ||
| Martin's ceanothus | CEMA2 | Ceanothus martinii | 0–20 | – | ||
| brickellbush | BRICK | Brickellia | 0–15 | – | ||
| littleleaf mountain mahogany | CEIN7 | Cercocarpus intricatus | 0–13 | – | ||
| rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–13 | – | ||
| Stansbury cliffrose | PUST | Purshia stansburiana | 0–13 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–13 | – | ||
| roundleaf buffaloberry | SHRO | Shepherdia rotundifolia | 0–12 | – | ||
| crispleaf buckwheat | ERCO14 | Eriogonum corymbosum | 0–10 | – | ||
| Fremont's mahonia | MAFR3 | Mahonia fremontii | 0–5 | – | ||
| spineless horsebrush | TECA2 | Tetradymia canescens | 0–5 | – | ||
| Torrey's jointfir | EPTO | Ephedra torreyana | 0–4 | – | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–3 | – | ||
| yellow rabbitbrush | CHVI8 | Chrysothamnus viscidiflorus | 0–3 | – | ||
| narrowleaf yucca | YUAN2 | Yucca angustissima | 0–3 | – | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–1 | – | ||
| Whipple's fishhook cactus | SCWH | Sclerocactus whipplei | 0–1 | – | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–1 | – | ||
|
Grass/Grasslike
|
||||||
| 3 | Dominant Grass | 15–75 | ||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–75 | – | ||
| saline wildrye | LESAS | Leymus salinus ssp. salinus | 0–75 | – | ||
| cheatgrass | BRTE | Bromus tectorum | 1–50 | – | ||
| James' galleta | PLJA | Pleuraphis jamesii | 5–48 | – | ||
| needle and thread | HECOC8 | Hesperostipa comata ssp. comata | 0–30 | – | ||
| 1 | Sub-dominant Grass | 0–20 | ||||
| Grass, annual | 2GA | Grass, annual | 0–20 | – | ||
| Grass, perennial | 2GP | Grass, perennial | 0–20 | – | ||
| slender wheatgrass | ELTR7 | Elymus trachycaulus | 0–20 | – | ||
| bluegrass | POA | Poa | 0–20 | – | ||
| New Mexico feathergrass | HENE5 | Hesperostipa neomexicana | 0–15 | – | ||
| desert needlegrass | ACSP12 | Achnatherum speciosum | 0–5 | – | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–5 | – | ||
|
Forb
|
||||||
| 2 | Forbs | 10–30 | ||||
| rock goldenrod | PEPU7 | Petradoria pumila | 0–24 | – | ||
| browneyed Susan | RUTR2 | Rudbeckia triloba | 0–13 | – | ||
| desert princesplume | STPI | Stanleya pinnata | 0–13 | – | ||
| Forb, annual | 2FA | Forb, annual | 0–10 | – | ||
| Forb, perennial | 2FP | Forb, perennial | 0–10 | – | ||
| Newberry's twinpod | PHNE5 | Physaria newberryi | 0–8 | – | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–8 | – | ||
| lobeleaf groundsel | PAMU11 | Packera multilobata | 0–8 | – | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–4 | – | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–3 | – | ||
| roughseed cryptantha | CRFL6 | Cryptantha flavoculata | 0–3 | – | ||
| larkspur | DELPH | Delphinium | 0–2 | – | ||
| wedgeleaf draba | DRCU | Draba cuneifolia | 0–2 | – | ||
| Wetherill's buckwheat | ERWE | Eriogonum wetherillii | 0–2 | – | ||
| beardtongue | PENST | Penstemon | 0–2 | – | ||
| primrose | PRIMU | Primula | 0–2 | – | ||
| thrift mock goldenweed | STAR10 | Stenotus armerioides | 0–2 | – | ||
| longbeak streptanthella | STLO4 | Streptanthella longirostris | 0–1 | – | ||
| gilia | GILIA | Gilia | 0–1 | – | ||
| pointed gumweed | GRFA | Grindelia fastigiata | 0–1 | – | ||
| woolly locoweed | ASMO7 | Astragalus mollissimus | 0–1 | – | ||
| Wright's bird's beak | COWR2 | Cordylanthus wrightii | 0–1 | – | ||
Table 20. Community 2.2 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Tree
|
||||||
| 1 | Dominant Tree | 20–50 | ||||
| Utah juniper | JUOS | Juniperus osteosperma | 3–50 | – | ||
| twoneedle pinyon | PIED | Pinus edulis | 0–5 | – | ||
|
Shrub/Vine
|
||||||
| 2 | Dominant Shrubs | 10–50 | ||||
| Bigelow sage | ARBI3 | Artemisia bigelovii | 0–30 | – | ||
| mormon tea | EPVI | Ephedra viridis | 0–10 | – | ||
| 3 | Sub-dominant Shrubs | 40–60 | ||||
| singleleaf ash | FRAN2 | Fraxinus anomala | 0–50 | – | ||
| yellow rabbitbrush | CHVI8 | Chrysothamnus viscidiflorus | 0–42 | – | ||
| Utah serviceberry | AMUT | Amelanchier utahensis | 0–40 | – | ||
| crispleaf buckwheat | ERCO14 | Eriogonum corymbosum | 0–30 | – | ||
| sumac | RHUS | Rhus | 0–30 | – | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–27 | – | ||
| blackbrush | CORA | Coleogyne ramosissima | 0–24 | – | ||
| Martin's ceanothus | CEMA2 | Ceanothus martinii | 0–20 | – | ||
| rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–13 | – | ||
| littleleaf mountain mahogany | CEIN7 | Cercocarpus intricatus | 0–13 | – | ||
| Stansbury cliffrose | PUST | Purshia stansburiana | 0–13 | – | ||
| roundleaf buffaloberry | SHRO | Shepherdia rotundifolia | 0–13 | – | ||
| brickellbush | BRICK | Brickellia | 0–10 | – | ||
| desert snowberry | SYLO | Symphoricarpos longiflorus | 0–8 | – | ||
| spineless horsebrush | TECA2 | Tetradymia canescens | 0–5 | – | ||
| Fremont's mahonia | MAFR3 | Mahonia fremontii | 0–5 | – | ||
| Torrey's jointfir | EPTO | Ephedra torreyana | 0–4 | – | ||
| narrowleaf yucca | YUAN2 | Yucca angustissima | 0–3 | – | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–3 | – | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–1 | – | ||
| Whipple's fishhook cactus | SCWH | Sclerocactus whipplei | 0–1 | – | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–1 | – | ||
|
Grass/Grasslike
|
||||||
| 3 | Dominant Grass | 25–60 | ||||
| saline wildrye | LESAS | Leymus salinus ssp. salinus | 0–50 | – | ||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–50 | – | ||
| cheatgrass | BRTE | Bromus tectorum | 1–50 | – | ||
| James' galleta | PLJA | Pleuraphis jamesii | 5–20 | – | ||
| 1 | Sub-dominant Grass | 0–20 | ||||
| Grass, annual | 2GA | Grass, annual | 0–20 | – | ||
| Grass, perennial | 2GP | Grass, perennial | 0–20 | – | ||
| slender wheatgrass | ELTR7 | Elymus trachycaulus | 0–20 | – | ||
| New Mexico feathergrass | HENE5 | Hesperostipa neomexicana | 0–13 | – | ||
| desert needlegrass | ACSP12 | Achnatherum speciosum | 0–8 | – | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–5 | – | ||
| bluegrass | POA | Poa | 0–5 | – | ||
|
Forb
|
||||||
| 2 | Forbs | 10–25 | ||||
| rock goldenrod | PEPU7 | Petradoria pumila | 0–24 | – | ||
| browneyed Susan | RUTR2 | Rudbeckia triloba | 0–13 | – | ||
| desert princesplume | STPI | Stanleya pinnata | 0–13 | – | ||
| Newberry's twinpod | PHNE5 | Physaria newberryi | 0–8 | – | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–8 | – | ||
| lobeleaf groundsel | PAMU11 | Packera multilobata | 0–8 | – | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–4 | – | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–3 | – | ||
| roughseed cryptantha | CRFL6 | Cryptantha flavoculata | 0–3 | – | ||
| larkspur | DELPH | Delphinium | 0–2 | – | ||
| wedgeleaf draba | DRCU | Draba cuneifolia | 0–2 | – | ||
| beardtongue | PENST | Penstemon | 0–2 | – | ||
| primrose | PRIMU | Primula | 0–2 | – | ||
| thrift mock goldenweed | STAR10 | Stenotus armerioides | 0–1 | – | ||
| longbeak streptanthella | STLO4 | Streptanthella longirostris | 0–1 | – | ||
| woolly locoweed | ASMO7 | Astragalus mollissimus | 0–1 | – | ||
| Wright's bird's beak | COWR2 | Cordylanthus wrightii | 0–1 | – | ||
| Wetherill's buckwheat | ERWE | Eriogonum wetherillii | 0–1 | – | ||
| gilia | GILIA | Gilia | 0–1 | – | ||
| pointed gumweed | GRFA | Grindelia fastigiata | 0–1 | – | ||
Interpretations
Animal community
--Wildlife Interpretation--
The very steep slopes and scarcity of water on this site limits its species richness and the abundance of large mammals. It does provide thermal cover and limited forage opportunities for mule deer. Birds, bats, lizards, snakes and rodents are quite common. Several species of birds can be found using this site. Golden eagles and red-tailed hawks are common as well as great horned-owls. Other species typical of pinyon juniper areas including black-chinned and rufous hummingbirds, several fly catchers, wood peckers, and corvids will use this site for nesting and foraging. Several species of rodents occupy this site including desert cottontail, black tailed jack rabbit, Colorado chipmunk, white–tailed Antelope squirrel, Apache pocket mouse, and several species of Peromyscus. Bats (Myotis, Pipisturellus, and others) can be observed in this ecological site, but are likely limited to areas near water or canyons.
--Grazing Interpretations—
This sites plant community primarily consists of a very sparse canopy of two-needle pinyon and Utah Juniper growing on very steep slopes. Common shrubs include Utah serviceberry, littleleaf mahogany, mormon tea and Bigelow’s sagebrush. Grasses include Indian ricegrass and James galleta.
These steep slopes seriously limit the sites use for livestock grazing. It's lack natural perennial water sources also reduces its suitability. Mule deer, desert bighorn sheep, pronghorn antelope, and elk may utilize this site to some degree, although in many places, their populations will be small and have little grazing impact.
Hydrological functions
The soils associated with this ecological site are generally in Hydrologic Soil Group B. Soils in this group have medium runoff potential when thoroughly wet; however, due to the steepness of this site, the runoff potential is high. Water movement through the soil is not restricted. Hydrological groups are used in equations that estimate runoff from rainfall. These estimates are needed for solving hydrologic problems that arise in planning watershed-protection and flood-prevention projects and for designing structures for the use, control and disposal of water. (NRCS National Engineering Handbook). In areas similar to the reference state where ground cover is adequate, infiltration is increased and runoff potential is decreased. In areas where ground cover is less, infiltration is reduced and runoff potential is increased.
Surface disturbance and compaction caused by ATV off-road vehicles tracks, and dirt roads can affect this sites hydrology. Any resulting compaction increases bulk density and breaks down soil aggregates. This results in decreased infiltration rates and increased runoff. The actual removal of the plants due to the tire tracks can alter the hydrology by decreasing plant cover and increasing bare ground. In the rare event that fire occurs on this site, it can also affect its hydrology, but these affects are highly variable. Fire intensity, fuel type, soil, climate, and topography can each have different influences. Fires can increase areas of bare ground and hydrophobic layers that reduce infiltration and increase runoff. (National Range and Pasture Handbook, 2003)
Different plant communities affect hydrology in different ways.
Recreational uses
Recreation activities include aesthetic value, bird viewing, hunting and hiking.
Wood products
Potential wood products include firewood and fenceposts; however, harvesting such products may be difficult due to steep slopes and sparse stands.
Other information
--Poisonous and Toxic Plant Communities--
Toxic plants associated with this site include woolly locoweed and broom snakeweed.
Woolly locoweed is toxic to all classes of livestock and wildlife. Locoweed is palatable and has a similar nutrient value as alfalfa, which may cause animals to consume it even when other forage is available. Locoweed contains swainsonine (indolizdine alkaloid) and is poisonous at all stages of growth. Poisoning will become evident after 2-3 weeks of continuous grazing and is associated with 4 major symptoms: 1) neurological damage, 2) emaciation, 3) reproductive failure and abortion, and 4) congestive heart failure linked with “high mountain disease”.
Broom snakeweed contains steroids, terpenoids, saponins, and flavones that can cause abortions or reproductive failure in sheep and cattle, however cattle are most susceptible. These toxins are most abundant during active growth and leafing stages. Cattle and sheep generally will only utilize broom snakeweed when other forage is unavailable, typically in winter when toxicity levels are at their lowest (Knight and Walter, 2001).
--Invasive Plant Communities--
As ecological conditions deteriorate and perennial vegetation decreases due to disturbance (fire, drought, off road vehicle overuse, erosion, etc.) annual forbs and grasses can invade the site. Of particular concern in semi-arid environments are annual invaders including red brome, cheatgrass, Russian thistle, kochia, halogeton, and annual mustards. The presence of these species will depend on soil properties and moisture availability; however, these invaders are highly adaptive and can flourish in many locations. Once established, complete removal is difficult, but suppression may be possible. On well developed Utah juniper and pinyon pine communities soils are completly occupied by lateral roots, which inhibit an herbaceous understory as well as annual invasions. However, once these sites are disturbed and pinyon-juniper communities begin to decline, invasion is possible.
--Fire Ecology--
The ability for an ecological site to carry fire depends primarily on the present fuel load and plant moisture content. Sites with small fuel loads will burn more slowly and less intensely than sites with large fuel loads. Many semi-desert communities in the Colorado Plateau may have evolved without a significient influence of fire. However, a year of exceptionally heavy winter rains can generate enough fuels by producing heavy stands of annual forbs and grasses to carry fire. When fires do occur, the effect on the plant community may be extreme due to the harsh environment and slow rate of recovery.
There is no evidence that this site historically mainained a short burn frequency. Only a few species show fire scars and can be aged. This ecological site is comprised of scatterd trees with bare interspaces to patchy occurrence of grasses and shrubs, which is unlikely to carry a fire unless under conditions of high winds, high temperature, and low humidity. Currently, burning is not a recommended brush management tool. If annual grasses or forbs dominate the area after disturbance, re-vegetating efforts could be hampered due to several factors including an increase in fire frequency.
Supporting information
Inventory data references
The data collected in 2005-2008 were in conjunction with the soil survey update for Arches and Canyonlands National Park. The vegetation data was collected in associated with a soil pit and geo-referenced. All the data is stored as hard copy files and in electronic format in the NRCS Utah State Office.
Type locality
| Location 1: San Juan County, UT | |
|---|---|
| UTM zone | N |
| UTM northing | 4244347 |
| UTM easting | 600766 |
| General legal description | Canyonlands National Park |
Other references
Betancourt, J. L., E. A. Pierson, K. A. Rylander, J. A. Fairchild-Parks, and J. S. Dean. 1993. Influence of history and climate on New Mexico pin˜on-juniper woodlands. Pages 42–62 in E. F. Aldon, and D. W. Shaw, editors. Managing pinon-juniper ecosystems for sustainability and social needs. USDA Forest Service Technical Report RM-236.
Knight, A.P. and R.G. Walter. 2001. A guide to plant poisoning of animals in North America. Teton NewMedia. Jackson, WY.
NPS.gov. 2008. Canyonlands National Park. Nature and Science. Available: http://www.nps.gov/cany/naturescience/. Accessed on January 4, 2008.
Relative Forage Preference of Plants for Grazing Use by Season: Plants commonly found in Major Land Resource Area D35 --The Colorado Plateau. 2007
Stubbendieck, J., S. L. Hatch, and C. H. Butterfield. 1997. North American range plants. Lincoln, NE: University of Nebraska Press. 501p.
USDA, Forest Service. 2007. Fire effects information: plant species life form. Available at http://www.fs.fed.us/database/feis/plants/index.html. Accessed 7 August 2007.
National Engineering Handbook. US Department of Agriculture, Natural Resources Conservation Service. Available: http://www.info.usda.gov/CED/Default.cfm#National%20Engineering%20Handbook. Accessed February 25, 2008.
NRCS Grazing Lands Technology Institute. 2003. National Range and Pasture Handbook. Fort Worth, TX, USA: US Department of Agriculture, Natural Resources Conservation Service, 190-VI-NRPH.
Contributors
Jacob Owens
V. Keith Wadman
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) | Jacob Owens (NRCS, Shane Green (NRCS) |
|---|---|
| Contact for lead author |
shane.green@ut.usda.gov |
| Date | 12/07/2009 |
| Approved by | Shane A. Green |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
Very few. Due to the surface rock fragments on this site, traditional rill formation is reduced. The overall gravelly to channery surface is expected to be resistant to rill formation and accelerated erosion in general. Where rills do occur, they may extend down entire slope. -
Presence of water flow patterns:
Due to the steep slopes, flow patterns are present and tend to be very sinuous and wind around rock fragments and perennial plant bases. They show some evidence of erosion with fines and litter depositing against the uphill side of gravel, rocks and plants. During episodic precipitation events e.g. thunderstorms, these sites are expected to shed large volumes of water to adjacent ecological sites. -
Number and height of erosional pedestals or terracettes:
Pedestals may form at the base of plants that occur on the edge of primary flow patterns and rills. Interspaces between any well developed biological soil crusts resemble pedestals and may be up to 2 inches high. Terracettes are present. Debris dams of small to medium sized litter (up to 2 inches in diameter) may form in water flow patterns, rills, and gullies. These debris dams may accumulate smaller litter (leaves, grass and forb stems). -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
8 – 30 %. Most bare ground is associated with water flow patterns, rills, and gullies. Soil is covered by up to 60 percent rock fragments. Any areas with well developed biological soil crusts should not be counted as bare ground. Poorly developed biological soil crusts that are interpreted as functioning as bare ground (therefore they would be susceptible to raindrop splash erosion) should be recorded as bare ground. Ground cover is based on first raindrop impact, and bare ground is the opposite of ground cover. -
Number of gullies and erosion associated with gullies:
Few gullies may be present. Length often extends from exposed bedrock until gully reaches a stream or an area where water and sediment accumulate, but they may be wide and shallow and armored with very large rocks. -
Extent of wind scoured, blowouts and/or depositional areas:
None. -
Amount of litter movement (describe size and distance expected to travel):
Due to the steepness of slope being between 30 to 70 percent, down slope redistribution of any incident litter caused by water is expected. Deposition would likely occur at points of obstruction such as the uphill side of gravel, rocks and plants, especially following major storm events. Fine litter is moved with even moderate precipitation events and spring runoff. Woody stems may be washed from site. Gullies may remove accumulated litter from under trees. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
80 to 90% of this site should have an erosion rating of 4 or 5. 10 to 20% may have a rating of 3 to 4. The average should be a 4. Surface texture is gravelly loam to very channery sandy loam. Vegetation cover, litter, biological soil crusts and surface rock reduce erosion. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Soil surface is 3 inches deep. Structure is weak fine platy to moderate fine and medium granular. Color is reddish brown (7.5YR5/4). The A horizon would be expected to be more strongly developed under plant canopies. It is important if you are sampling to observe the A horizon under plant canopies as well as the interspaces. Use the specific information for the soil you are assessing found in the published soil survey to supplement this description. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Spatial distribution of plants and/or well developed biological soil crusts (where present) intercept raindrops reducing splash erosion and provide areas of surface detention to store water allowing additional time for infiltration. Crowns of trees and accumulating litter at base of trees appear to create a micro-topography that may enhance development of water flow patterns below the drip line of the canopy. Significant increases in Pinyon-juniper canopy (beyond the reference state) reduces understory vegetation causing an associated increase in runoff. -
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
None. There may be layers of calcium carbonate, gravel, cobbles or other naturally occurring hard layers found in the soil subsurface. These should not be considered to be compaction layers. -
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:
Dominance by average annual production: Trees (Juniper > Pinion) > Sprouting shrubs > Cool season perennial grasses > Warm season perennial grasses > forbs. Functional/structural groups may appropriately contain non-native species if their ecological function is the same as the native species in the reference state (e.g. Crested wheatgrass, Intermediate wheatgrass, etc.)Sub-dominant:
Other:
Biological soil crust is variable in it’s expression where present on this site and is measured as a component of ground cover.Additional:
Following a recent disturbance such as fire, drought, or insects that removes the woody vegetation, forbs and perennial grasses (herbaceous species) may dominate the community. If a disturbance has not occurred for an extended period of time, woody species may continue to increase crowding out the perennial herbaceous understory species. In either case, these conditions would reflect a functional community phase within the reference state.
Dominants— Utah juniper, two-needle pinion, Bigelow’s sagebrush, mormon tea, and Indian ricegrass. Sub Dominants— Broom snakeweed, Single leaf ash, roundleaf buffalo berry, James galleta. Perennial and annual forbs can be expected to vary widely in their expression in the plant community based upon departures from average growing conditions.
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Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
In general, a mix of age classes may be expected with a few dead and decadent plants present. -
Average percent litter cover (%) and depth ( in):
Litter cover 2-5%. Variability may occur due to weather. -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
150-320 #/acre on an average year. -
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:
Possible invaders or increasers on this site are cheatgrass, sunflower, and halogeton, locoweed, broom snakeweed and juniper. -
Perennial plant reproductive capability:
All perennial plants should have the ability to reproduce sexually or asexually in most years, except in drought years.
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The Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.
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