Natural Resources
Conservation Service
Ecological site R035XY015UT
Sandy Bottom
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.
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.
Ecological site concept
Site concept: The Sandy Bottom (Fourwing Saltbush) ecological site recieves extra run-in water due to its landscape position on flood plains, stream terraces, and valley flats. It is found in the desert and semidesert climate zones of the Colorado and Green River Plateaus region (MLRA 35). The soils are deep alluvial deposits derived primarily from sandstone parent material. Soil textures range from sandy loams to fine sands throughout the profile and may have small gravel lenses. These soils are most often classified as fluvents, with mesic soil moisture regimes and aridic soil temperature regimes (occaisionally ustic aridic). The reference plant community is dominated by fourwing saltbush, Indian ricegrass, James' galleta, Sporobolus spp., and sometimes needle-and-thread. Herbivory, fire, drought, and invasive species are common drivers of plant community change on this site. Cheatgrass and Russian thistle are common invaders of the understory.
Associated sites
| R035XY003UT |
Alkali Bottom (Greasewood) This site usually occurs on soils with finer textures and higher salt content, but the two sites can be found in the same drainages where gradients in soil texture and salinity occur. |
|---|---|
| R035XY011UT |
Loamy Bottom (Basin Big Sagebrush) This site usually receives more annual precipitation and always occurs near a stream or drainageway. The two sites can occur together on stream terraces with sandy loam soil textures that average around 9 inches of precipitation. |
Similar sites
| R035XY212UT |
Semidesert Sand (Fourwing Saltbush) This site always has deep sandy soils and does not receive extra run-in water due to a more elevated landscape position. It usually has lower annual production and is less resistant to invasive species dominance and wind erosion. |
|---|---|
| R035XY215UT |
Semidesert Sandy Loam (4-Wing Saltbush) This site does not receive extra run-in water due to its landscape position. It occurs on similar soils with annual precipitation as low as 8 inches, but it usually has lower total production and is less resistant to invasive annual dominance. |
| R035XY011UT |
Loamy Bottom (Basin Big Sagebrush) This site is also a run-in site that can occur on deep, sandy loam alluvial deposits. However, this site averages 9-14 inches of annual precipitation and supports basin big sagebrush. |
Table 1. Dominant plant species
| Tree |
Not specified |
|---|---|
| Shrub |
(1) Atriplex canescens |
| Herbaceous |
(1) Achnatherum hymenoides |
Physiographic features
This site recieves extra run-in water due to its landscape position on flood plains, stream terraces, narrow valleys, and valley flats. Run off is low due to gentle slopes and highly permeable soils. The elevation ranges from 3800 to 6000 ft. This site usually does not have a seasonally high water table, but in some areas spring water table can be within 42 inches of the soil surface.
Table 2. Representative physiographic features
| Landforms |
(1)
Flood plain
(2) Valley (3) Channel |
|---|---|
| Flooding duration | Extremely brief (0.1 to 4 hours) to very brief (4 to 48 hours) |
| Flooding frequency | None to occasional |
| Ponding frequency | None |
| Elevation | 1,158 – 1,829 m |
| Slope | 0 – 5% |
| Aspect | Aspect is not a significant factor |
Climatic features
The climate is characterized by hot, dry summers and cool winters. Average annual precipitation ranges from 6.5 to 10 inches. Approximately 75% of the total precipitation occurs from March to October, mostly in the form of convection thunderstorms from July through October. June is typically the driest month during the growing season.
Large fluctuations in daily temperatures are common. Summer temperatures are in the 90's and winter temperatures are in the 20's and 30's. In addition to the climate stations listed below, the PRISM climate model was used to refine annual precipitation information.
Table 3. Representative climatic features
| Frost-free period (average) | 182 days |
|---|---|
| Freeze-free period (average) | 211 days |
| Precipitation total (average) | 254 mm |
Figure 2. Monthly precipitation range
Figure 3. Monthly average minimum and maximum temperature
Influencing water features
This site may be associated with riparian ecological sites, but does not support riparian-obligate vegetation.
Soil features
The soils are deep to very deep and well drained to somewhat excessively well drained. Surface and subsurface textures are generally fine sandy loams, loamy fine sands, and fine sands. There are typically few rock fragments on the soil surface and throughout the profile, but sometimes gravel lenses are present. These soils are usually formed in alluvium derived from sandstone parent materials. The soil temperature regime is mesic and the soil moisture regime is aridic (sometimes ustic aridic). Soils are nonsaline to slightly saline. Water-holding capacity ranges from 2.7 to 5.7 inches of water in the upper 40 inches of soil.
Major Soils Associated With This Site (Soil Survey Area + Series Name):
UT631 – Henry Mountains Area – Glenberg Family
UT633 – Canyonlands Area – Trail
UT638 – San Juan County, Central –Bankard Family
UT642 – Kane County – Trail
UT643 – San Juan County, Navajo Indian Reservation – Trail; Aneth
UT685 – Capital Reef National Park – Mido family;
UT686 – Escalante Grand Staircase National Monument – Trail; Suwanee
UT687 – Arches National Park – Livan Family
UT688 – Grand Canyon National Park – Sheppard
Table 4. Representative soil features
| Parent material |
(1)
Alluvium
–
sandstone
|
|---|---|
| Surface texture |
(1) Fine sandy loam (2) Loamy fine sand (3) Fine sand |
| Family particle size |
(1) Sandy |
| Drainage class | Well drained to somewhat excessively drained |
| Permeability class | Moderate to rapid |
| Soil depth | 152 cm |
| Surface fragment cover <=3" | 0 – 11% |
| Surface fragment cover >3" | 0 – 3% |
| Available water capacity (0-101.6cm) |
6.86 – 14.48 cm |
| Calcium carbonate equivalent (0-101.6cm) |
1 – 15% |
| Electrical conductivity (0-101.6cm) |
0 – 8 mmhos/cm |
| Sodium adsorption ratio (0-101.6cm) |
0 – 5 |
| Subsurface fragment volume <=3" (Depth not specified) |
0 – 12% |
| Subsurface fragment volume >3" (Depth not specified) |
0 – 3% |
Ecological dynamics
This site is historically dominated by fourwing saltbush and a diverse perennial grass understory dominated by Indian ricegrass, James's Galleta, Sporobolus spp, and/or needle-and-thread. The historic fire return interval is presumed to be about 35-100 years (Howard 2003). Fourwing saltbush and native grasses would have resprouted within one year following fire and maintained dominance of the site. There is no evidence that prolonged drought would dramatically alter the species composition of the site in reference condition, although production is expected to be lower. Inundation, persistent heavy browsing, and/or insect herbivory would have resulted in reduced fourwing saltbush and a grass-dominated plant community.
Today this site often burns less frequently due to fire suppression efforts and reduced fine fuel loads resulting from livestock grazing. In addition, excessive livestock grazing during the spring and summer can cause native grasses and forbs to lose vigor or disappear from the community completely.
Invasive plant species, particularly cheatgrass, Russian thistle, and annual mustards, can establish on the site given a seed source and germination sites in disturbed soil. These invasive annuals require little or no disturbance to establish, although disturbances often provide germination sites and/or seed sources that accelerate invasion.
When the ecological processes are altered due to improper grazing, prolonged drought, altered fire regime, invasive species dominance, and/or other disturbances, alternative states can occur that differ from the historic reference state in both plant community structure and ecological function.
State and transition model
Figure 4. State-and-Transition Model
More interactive model formats are also available.
View Interactive Models
More interactive model formats are also available.
View Interactive Models
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 3 submodel, plant communities
State 1
Reference State
The reference state contains plant communities presumed to occur on the Sandy Bottom site prior to the introduction of non-native plants, livestock grazing, and other modern disturbances. The reference state is generally dominated by fourwing saltbush and deep-rooted perennial bunchgrasses. Plant species are adapted to poorly developed, coarse soils. The reference state does not include any non-native or invasive plant species. Once invasive plants establish, return to the reference state may not be possible.
Community 1.1
Fourwing Saltbush/Perennial Grass
Figure 5. Phase 1.1
Community phase 1.1 is characterized by a fourwing saltbush canopy with diverse perennial grasses and forbs in the interspaces. The fire-return interval for this phase is 35-100 years, which triggers vigorous re-sprouting of fourwing saltbush and perennial grasses within one year following fire. Composition by air-dry weight is 35-60% grasses, 5-15% forbs, and 35-60% shrubs.
Figure 6. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Annual production by plant type
| Plant type | Low (kg/hectare) |
Representative value (kg/hectare) |
High (kg/hectare) |
|---|---|---|---|
| Grass/Grasslike | 168 | 280 | 392 |
| Shrub/Vine | 157 | 224 | 280 |
| Forb | 11 | 28 | 56 |
| Total | 336 | 532 | 728 |
Table 6. Ground cover
| Tree foliar cover | 0% |
|---|---|
| Shrub/vine/liana foliar cover | 10-25% |
| Grass/grasslike foliar cover | 15-30% |
| Forb foliar cover | 2-10% |
| Non-vascular plants | 0% |
| Biological crusts | 5-15% |
| Litter | 15-30% |
| Surface fragments >0.25" and <=3" | 0-12% |
| Surface fragments >3" | 0-3% |
| Bedrock | 0% |
| Water | 0% |
| Bare ground | 20-30% |
Table 7. Canopy structure (% cover)
| Height Above Ground (m) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.15 | – | – | 0-5% | 0-5% |
| >0.15 <= 0.3 | – | – | 0-5% | 0-5% |
| >0.3 <= 0.6 | – | 5-15% | 10-25% | 0-5% |
| >0.6 <= 1.4 | – | 10-20% | 0-5% | – |
| >1.4 <= 4 | – | – | – | – |
| >4 <= 12 | – | – | – | – |
| >12 <= 24 | – | – | – | – |
| >24 <= 37 | – | – | – | – |
| >37 | – | – | – | – |
Community 1.2
Perrenial Grass
Figure 7. Phase 1.2
Deep-rooted perennial bunchgrasses dominate the site. Fourwing saltbush is not dominant due to persistent heavy browsing over many years, insect herbivory, or prolonged anaerobic soil conditions (flooding). Percent composition by air-dry weight is 65-95% perennial grasses, 5-10% forbs, and 0-30% shrubs.
Figure 8. Annual production by plant type (representative values) or group (midpoint values)
Table 8. Annual production by plant type
| Plant type | Low (kg/hectare) |
Representative value (kg/hectare) |
High (kg/hectare) |
|---|---|---|---|
| Grass/Grasslike | 336 | 560 | 785 |
| Shrub/Vine | 28 | 56 | 112 |
| Forb | 11 | 28 | 56 |
| Total | 375 | 644 | 953 |
Table 9. Ground cover
| Tree foliar cover | 0% |
|---|---|
| Shrub/vine/liana foliar cover | 5-10% |
| Grass/grasslike foliar cover | 25-40% |
| Forb foliar cover | 2-10% |
| Non-vascular plants | 0% |
| Biological crusts | 5-20% |
| Litter | 5-15% |
| Surface fragments >0.25" and <=3" | 0-12% |
| Surface fragments >3" | 0-3% |
| Bedrock | 0% |
| Water | 0% |
| Bare ground | 30-45% |
Table 10. Canopy structure (% cover)
| Height Above Ground (m) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.15 | – | – | 0-5% | 0-5% |
| >0.15 <= 0.3 | – | – | 0-5% | 0-5% |
| >0.3 <= 0.6 | – | 0-10% | 20-40% | 0-5% |
| >0.6 <= 1.4 | – | 0-5% | 0-5% | – |
| >1.4 <= 4 | – | – | – | – |
| >4 <= 12 | – | – | – | – |
| >12 <= 24 | – | – | – | – |
| >24 <= 37 | – | – | – | – |
| >37 | – | – | – | – |
Pathway 1.1a
Community 1.1 to 1.2
This community pathway occurs when persistent heavy browsing, insect herbivory, or prolonged inundation of fourwing saltbush results in a perennial grass-dominated plant community.
Pathway 1.2a
Community 1.2 to 1.1
This pathway is the natural increase in fourwing saltbush until the shrub again co-dominates the site. It occurs when fourwing saltbush is not subjected to persisitent heavy browse, insect herbivory, or innundation for many years.
State 2
Invaded State
The invaded state is similar to the reference state in composition and ecological function, but allows for non-native species to be present. It also includes an at-risk plant community with reduced perennial grass production. When perennial grasses are losing vigor and the ability to propagate themselves, this state is at risk of transitioning to the depleted understory state, which is incapable of recovering perennial grasses without significant management inputs.
Community 2.1
Fourwing Saltbush/Perennial Grass
Figure 9. Phase 2.1
Phase 2.1 is similar to the reference plant community in composition and ecological function, but it allows for the presence of non-native/invasive species. It is dominated by fourwing saltbush and perennial grasses. Percent composition by air-dry weight is 35-60% perennial grasses, 5-15% forbs, and 35-60% shrubs.
Figure 10. Annual production by plant type (representative values) or group (midpoint values)
Table 11. Annual production by plant type
| Plant type | Low (kg/hectare) |
Representative value (kg/hectare) |
High (kg/hectare) |
|---|---|---|---|
| Grass/Grasslike | 168 | 280 | 392 |
| Shrub/Vine | 157 | 224 | 280 |
| Forb | 11 | 28 | 56 |
| Total | 336 | 532 | 728 |
Table 12. Ground cover
| Tree foliar cover | 0% |
|---|---|
| Shrub/vine/liana foliar cover | 10-25% |
| Grass/grasslike foliar cover | 15-30% |
| Forb foliar cover | 2-10% |
| Non-vascular plants | 0% |
| Biological crusts | 5-15% |
| Litter | 15-30% |
| Surface fragments >0.25" and <=3" | 0-12% |
| Surface fragments >3" | 0-3% |
| Bedrock | 0% |
| Water | 0% |
| Bare ground | 20-30% |
Table 13. Canopy structure (% cover)
| Height Above Ground (m) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.15 | – | – | 0-5% | 0-5% |
| >0.15 <= 0.3 | – | – | 0-5% | 0-5% |
| >0.3 <= 0.6 | – | 5-15% | 10-25% | 0-5% |
| >0.6 <= 1.4 | – | 10-20% | 0-5% | – |
| >1.4 <= 4 | – | – | – | – |
| >4 <= 12 | – | – | – | – |
| >12 <= 24 | – | – | – | – |
| >24 <= 37 | – | – | – | – |
| >37 | – | – | – | – |
Community 2.2
Perennial Shrubland/Grassland
Figure 11. Phase 2.2
This plant community is similar to phase 1.2 in structure and function, but it allows for non-native/invasive species to be present. Deep-rooted perennial bunchgrasses dominate the site. Fourwing saltbush is not dominant due to persistent heavy browsing over many years, insect herbivory, or prolonged anaerobic soil conditions (flooding). Percent composition by air-dry weight is 65-95% perennial grasses, 5-10% forbs, and 0-30% shrubs.
Figure 12. Annual production by plant type (representative values) or group (midpoint values)
Table 14. Annual production by plant type
| Plant type | Low (kg/hectare) |
Representative value (kg/hectare) |
High (kg/hectare) |
|---|---|---|---|
| Grass/Grasslike | 336 | 560 | 785 |
| Shrub/Vine | 28 | 56 | 112 |
| Forb | 11 | 28 | 56 |
| Total | 375 | 644 | 953 |
Table 15. Ground cover
| Tree foliar cover | 0% |
|---|---|
| Shrub/vine/liana foliar cover | 5-10% |
| Grass/grasslike foliar cover | 25-40% |
| Forb foliar cover | 2-10% |
| Non-vascular plants | 0% |
| Biological crusts | 5-20% |
| Litter | 5-15% |
| Surface fragments >0.25" and <=3" | 0-12% |
| Surface fragments >3" | 0-3% |
| Bedrock | 0% |
| Water | 0% |
| Bare ground | 30-45% |
Table 16. Canopy structure (% cover)
| Height Above Ground (m) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.15 | – | – | 0-5% | 0-5% |
| >0.15 <= 0.3 | – | – | 0-5% | 0-5% |
| >0.3 <= 0.6 | – | 0-10% | 20-40% | 0-5% |
| >0.6 <= 1.4 | – | 0-5% | 0-5% | – |
| >1.4 <= 4 | – | – | – | – |
| >4 <= 12 | – | – | – | – |
| >12 <= 24 | – | – | – | – |
| >24 <= 37 | – | – | – | – |
| >37 | – | – | – | – |
Community 2.3
Fourwing Saltbush/Reduced Perennial Grasses
Figure 13. Phase 2.3
This plant community is at-risk of crossing a threshold into the depleted understory state (state 3). Years of excessive grazing of perennial grasses during growth has favored non-native invasive species, primarily cheatgrass and/or Russian thistle, to co-dominate the understory. Prescribed grazing is required to improve the reproductive capability of perennial grasses and avoid the transition to state 3. Percent composition by air-dry weight is 10-30% perennial grasses and forbs, 10-30% annual grasses and forbs, and 50-70% shrubs.
Figure 14. Annual production by plant type (representative values) or group (midpoint values)
Table 17. Annual production by plant type
| Plant type | Low (kg/hectare) |
Representative value (kg/hectare) |
High (kg/hectare) |
|---|---|---|---|
| Shrub/Vine | 168 | 224 | 280 |
| Forb | 28 | 84 | 140 |
| Grass/Grasslike | 56 | 84 | 112 |
| Total | 252 | 392 | 532 |
Table 18. Ground cover
| Tree foliar cover | 0-1% |
|---|---|
| Shrub/vine/liana foliar cover | 10-20% |
| Grass/grasslike foliar cover | 10-40% |
| Forb foliar cover | 2-11% |
| Non-vascular plants | 0% |
| Biological crusts | 20-50% |
| Litter | 3-7% |
| Surface fragments >0.25" and <=3" | 0-13% |
| Surface fragments >3" | 0-3% |
| Bedrock | 0% |
| Water | 0% |
| Bare ground | 6-40% |
Table 19. Canopy structure (% cover)
| Height Above Ground (m) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
|---|---|---|---|---|
| <0.15 | – | – | 0-10% | 0-10% |
| >0.15 <= 0.3 | – | – | 0-20% | 5-10% |
| >0.3 <= 0.6 | – | 5-20% | 10-20% | 0-15% |
| >0.6 <= 1.4 | – | 5-10% | – | – |
| >1.4 <= 4 | 0-1% | – | – | – |
| >4 <= 12 | – | – | – | – |
| >12 <= 24 | – | – | – | – |
| >24 <= 37 | – | – | – | – |
| >37 | – | – | – | – |
Pathway 2.1a
Community 2.1 to 2.2
This community pathway occurs when persistent heavy browsing, insect herbivory, or prolonged inundation of fourwing saltbush results in a perennial grass-dominated plant community.
Pathway 2.1b
Community 2.1 to 2.3
This pathway occurs when perennial grasses are reduced in the understory due to excessive grazing during the growing period. Perennial grasses are losing their ability to propagate themselves, and non-native species may co-dominate the understory.
Pathway 2.2a
Community 2.2 to 2.1
This pathway is the natural increase in fourwing saltbush until the shrub again co-dominates the site. It occurs when fourwing saltbush is not subjected to persisitent heavy browse, insect herbivory, or innundation for many years.
Pathway 2.3a
Community 2.3 to 2.2
This pathway is facilitated by prescribed grazing that provides rest during the growth period for perennial grasses to improve their vigor and reproductive capacity. This will require at least one above average precipitation year, or many average precipitation years to complete.
State 3
Depleted Understory State
The depleted understory state occurs when perennial grasses have been lost from the understory. Perennial forbs may also be reduced. Interspaces may be sparsely vegetated or dominated by Russian thistle or other annual invasive species. Fire in perpetuates this state, since fourwing saltbush and invasive annuals are both capable of recovering quickly following fire.
Community 3.1
Fourwing Saltbush/Forb Understory
Figure 15. Phase 3.1
This phase occurs when perennial grasses are no longer dominant in the understory and annual forbs dominate the shrub interspaces. Percent composition by air-dry weight is 0-5% grasses, 35-50% annual forbs, and 45-65% shrubs.
Community 3.2
Fourwing Saltbush/Annual Grass Understory
Figure 16. Phase 3.2
This community occurs when perennial grasses no longer dominate the understory and recent fire and/or above average spring precipitation favors cheatgrass reproduction and establishment.
Pathway 3.1a
Community 3.1 to 3.2
This pathway occurs when above average spring precipitation and below average summer precipitation favors cheatgrass over annual forbs.
Pathway 3.2a
Community 3.2 to 3.1
This pathway may occur in years with low spring moisture and high summer precipitation.
Transition T1a
State 1 to 2
Establishment and persistence of non-native species results in a transition from the reference state to the invaded state.
Transition T2a
State 2 to 3
This transition occurs when perennial grasses are reduced by improper grazing to the point that they can no longer self-propagate. Few remnant plants may still persist under shrubs, but re-establishment and dominance by perennial grasses will not occur following a fire, or with the removal of livestock grazing.
Additional community tables
Table 20. Community 1.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Shrub/Vine
|
||||||
| 0 | Dominant Shrubs | 157–280 | ||||
| fourwing saltbush | ATCA2 | Atriplex canescens | 157–280 | 8–15 | ||
| 3 | Sub-dominant shrubs | 0–112 | ||||
| Shrub (>.5m) | 2SHRUB | Shrub (>.5m) | 0–34 | 0–4 | ||
| rubber rabbitbrush | ERNAN5 | Ericameria nauseosa ssp. nauseosa var. nauseosa | 0–34 | 0–3 | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–22 | 0–2 | ||
| sand sagebrush | ARFI2 | Artemisia filifolia | 0–17 | 0–3 | ||
| basin big sagebrush | ARTRT | Artemisia tridentata ssp. tridentata | 0–17 | 0–2 | ||
| shadscale saltbush | ATCO | Atriplex confertifolia | 0–17 | 0–2 | ||
| Torrey's jointfir | EPTO | Ephedra torreyana | 0–11 | 0–2 | ||
| desert pepperweed | LEFR2 | Lepidium fremontii | 0–11 | 0–2 | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–11 | 0–2 | ||
| frosted mint | POIN3 | Poliomintha incana | 0–11 | 0–2 | ||
| skunkbush sumac | RHTRT | Rhus trilobata var. trilobata | 0–11 | 0–2 | ||
| greasewood | SAVE4 | Sarcobatus vermiculatus | 0–11 | 0–2 | ||
|
Grass/Grasslike
|
||||||
| 0 | Dominant Grasses | 140–392 | ||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–146 | 0–15 | ||
| needle and thread | HECO26 | Hesperostipa comata | 0–146 | 0–15 | ||
| James' galleta | PLJA | Pleuraphis jamesii | 0–112 | 0–10 | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–90 | 0–6 | ||
| mesa dropseed | SPFL2 | Sporobolus flexuosus | 0–90 | 0–6 | ||
| 1 | Sub-dominant Grasses | 0–56 | ||||
| squirreltail | ELEL5 | Elymus elymoides | 0–11 | 0–1 | ||
| contorted sphagnum | SPCO14 | Sphagnum contortum | 0–11 | 0–1 | ||
| spike dropseed | SPCO4 | Sporobolus contractus | 0–11 | 0–1 | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–6 | 0–1 | ||
| saltgrass | DISP | Distichlis spicata | 0–6 | 0–1 | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–6 | 0–1 | ||
| low woollygrass | DAPU7 | Dasyochloa pulchella | 0–4 | 0–1 | ||
| giant dropseed | SPGI | Sporobolus giganteus | 0–2 | 0–1 | ||
|
Forb
|
||||||
| 2 | Forbs | 11–56 | ||||
| seepweed | SUAED | Suaeda | 0–45 | 0–5 | ||
| Forb, annual | 2FA | Forb, annual | 0–34 | – | ||
| Forb, perennial | 2FP | Forb, perennial | 0–34 | – | ||
| bastard toadflax | COUM | Comandra umbellata | 0–17 | 0–5 | ||
| povertyweed | IVAX | Iva axillaris | 0–11 | 0–5 | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–11 | 0–2 | ||
| flatspine bur ragweed | AMAC2 | Ambrosia acanthicarpa | 0–11 | 0–2 | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–9 | 0–2 | ||
| gooseberryleaf globemallow | SPGR2 | Sphaeralcea grossulariifolia | 0–9 | 0–1 | ||
| Pacific aster | SYCHC | Symphyotrichum chilense var. chilense | 0–6 | 0–2 | ||
| woolly plantain | PLPA2 | Plantago patagonica | 0–6 | 0–2 | ||
| flatspine stickseed | LAOC3 | Lappula occidentalis | 0–6 | 0–2 | ||
| rusty lupine | LUPU | Lupinus pusillus | 0–6 | 0–2 | ||
| Crescent milkvetch | ASAM5 | Astragalus amphioxys | 0–6 | 0–1 | ||
| skyblue phacelia | PHCO | Phacelia coerulea | 0–6 | 0–1 | ||
| James' buckwheat | ERJA | Eriogonum jamesii | 0–6 | 0–1 | ||
| pale evening primrose | OEPA | Oenothera pallida | 0–3 | 0–1 | ||
| plains springparsley | CYAC | Cymopterus acaulis | 0–3 | 0–1 | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–3 | 0–1 | ||
| Fremont cottonwood | POFR2 | Populus fremontii | 0–3 | – | ||
| hoary tansyaster | MACA2 | Machaeranthera canescens | 0–2 | 0–1 | ||
| tufted evening primrose | OECA10 | Oenothera caespitosa | 0–2 | 0–1 | ||
| snowball sand verbena | ABFR2 | Abronia fragrans | 0–2 | 0–1 | ||
| water hemlock | CICUT | Cicuta | 0–1 | 0–1 | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–1 | 0–1 | ||
| desert princesplume | STPI | Stanleya pinnata | 0–1 | 0–1 | ||
Table 21. Community 1.2 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 0 | Dominant Grasses | 336–785 | ||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–560 | 0–20 | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–560 | 0–20 | ||
| needle and thread | HECO26 | Hesperostipa comata | 0–224 | 0–15 | ||
| mesa dropseed | SPFL2 | Sporobolus flexuosus | 0–112 | 0–6 | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 45–90 | 0–5 | ||
| James' galleta | PLJA | Pleuraphis jamesii | 0–45 | 0–3 | ||
| scarlet globemallow | SPCO | Sphaeralcea coccinea | 19–37 | – | ||
| 1 | Sub-Dominant Grass | 0–56 | ||||
| spike dropseed | SPCO4 | Sporobolus contractus | 0–11 | 0–1 | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–11 | 0–1 | ||
| blue grama | BOGR2 | Bouteloua gracilis | 0–6 | 0–1 | ||
| low woollygrass | DAPU7 | Dasyochloa pulchella | 0–1 | 0–1 | ||
| saltgrass | DISP | Distichlis spicata | 0–1 | 0–1 | ||
| squirreltail | ELEL5 | Elymus elymoides | 0–1 | 0–1 | ||
| contorted sphagnum | SPCO14 | Sphagnum contortum | 0–1 | 0–1 | ||
| giant dropseed | SPGI | Sporobolus giganteus | 0–1 | 0–1 | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–1 | 0–1 | ||
|
Forb
|
||||||
| 2 | Forbs | 11–56 | ||||
| Mojave seablite | SUMO | Suaeda moquinii | 0–45 | 0–5 | ||
| Forb, annual | 2FA | Forb, annual | 0–34 | 0–3 | ||
| Forb, perennial | 2FP | Forb, perennial | 0–34 | 0–3 | ||
| bastard toadflax | COUM | Comandra umbellata | 0–17 | 0–2 | ||
| rayless tansyaster | MAGR2 | Machaeranthera grindelioides | 0–17 | 0–2 | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–11 | 0–2 | ||
| povertyweed | IVAX | Iva axillaris | 0–11 | 0–2 | ||
| flatspine bur ragweed | AMAC2 | Ambrosia acanthicarpa | 0–11 | 0–2 | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–9 | 0–3 | ||
| gooseberryleaf globemallow | SPGR2 | Sphaeralcea grossulariifolia | 0–9 | 0–1 | ||
| Crescent milkvetch | ASAM5 | Astragalus amphioxys | 0–6 | 0–3 | ||
| flatspine stickseed | LAOC3 | Lappula occidentalis | 0–6 | 0–2 | ||
| woolly plantain | PLPA2 | Plantago patagonica | 0–6 | 0–2 | ||
| rusty lupine | LUPU | Lupinus pusillus | 0–6 | 0–2 | ||
| Pacific aster | SYCHC | Symphyotrichum chilense var. chilense | 0–6 | 0–2 | ||
| skyblue phacelia | PHCO | Phacelia coerulea | 0–6 | 0–1 | ||
| James' buckwheat | ERJA | Eriogonum jamesii | 0–6 | 0–1 | ||
| curlycup gumweed | GRSQ | Grindelia squarrosa | 0–6 | 0–1 | ||
| plains springparsley | CYAC | Cymopterus acaulis | 0–3 | 0–1 | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–3 | 0–1 | ||
| pale evening primrose | OEPA | Oenothera pallida | 0–3 | 0–1 | ||
| tufted evening primrose | OECA10 | Oenothera caespitosa | 0–2 | 0–1 | ||
| snowball sand verbena | ABFR2 | Abronia fragrans | 0–2 | 0–1 | ||
| water hemlock | CICUT | Cicuta | 0–1 | 0–1 | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–1 | 0–1 | ||
| desert princesplume | STPI | Stanleya pinnata | 0–1 | 0–1 | ||
|
Shrub/Vine
|
||||||
| 3 | Shrubs | 28–112 | ||||
| rubber rabbitbrush | ERNAN5 | Ericameria nauseosa ssp. nauseosa var. nauseosa | 0–101 | 0–8 | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–45 | 0–4 | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–28 | 0–3 | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–11 | 0–2 | ||
| greasewood | SAVE4 | Sarcobatus vermiculatus | 0–11 | 0–1 | ||
| desert pepperweed | LEFR2 | Lepidium fremontii | 0–6 | 0–2 | ||
| shadscale saltbush | ATCO | Atriplex confertifolia | 0–6 | 0–2 | ||
| sand sagebrush | ARFI2 | Artemisia filifolia | 0–2 | 0–1 | ||
| Stansbury cliffrose | PUST | Purshia stansburiana | 0–2 | 0–1 | ||
| basin big sagebrush | ARTRT | Artemisia tridentata ssp. tridentata | 0–1 | 0–1 | ||
|
Tree
|
||||||
| 4 | Trees | 0–3 | ||||
| Fremont cottonwood | POFR2 | Populus fremontii | 0–3 | – | ||
Table 22. Community 2.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Shrub/Vine
|
||||||
| 0 | Dominant Shrubs | 157–280 | ||||
| fourwing saltbush | ATCA2 | Atriplex canescens | 157–280 | 8–15 | ||
| 3 | Sub-Dominant Shrubs | 0–112 | ||||
| rubber rabbitbrush | ERNAN5 | Ericameria nauseosa ssp. nauseosa var. nauseosa | 0–56 | 0–5 | ||
| desert pepperweed | LEFR2 | Lepidium fremontii | 0–45 | 0–2 | ||
| Shrub (>.5m) | 2SHRUB | Shrub (>.5m) | 0–34 | 0–3 | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–22 | 0–2 | ||
| sand sagebrush | ARFI2 | Artemisia filifolia | 0–17 | 0–2 | ||
| basin big sagebrush | ARTRT | Artemisia tridentata ssp. tridentata | 0–17 | 0–2 | ||
| shadscale saltbush | ATCO | Atriplex confertifolia | 0–17 | 0–2 | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–11 | 0–2 | ||
| frosted mint | POIN3 | Poliomintha incana | 0–11 | 0–2 | ||
| greasewood | SAVE4 | Sarcobatus vermiculatus | 0–11 | 0–2 | ||
| Torrey's jointfir | EPTO | Ephedra torreyana | 0–11 | 0–1 | ||
|
Grass/Grasslike
|
||||||
| 0 | Dominant Grasses | 140–392 | ||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–146 | 0–15 | ||
| needle and thread | HECO26 | Hesperostipa comata | 0–146 | 1–15 | ||
| James' galleta | PLJA | Pleuraphis jamesii | 0–112 | 0–10 | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–90 | 0–6 | ||
| mesa dropseed | SPFL2 | Sporobolus flexuosus | 0–90 | 0–6 | ||
| 1 | Sub-dominant Grasses | 0–56 | ||||
| cheatgrass | BRTE | Bromus tectorum | 0–45 | 0–5 | ||
| squirreltail | ELEL5 | Elymus elymoides | 0–11 | 0–1 | ||
| contorted sphagnum | SPCO14 | Sphagnum contortum | 0–11 | 0–1 | ||
| spike dropseed | SPCO4 | Sporobolus contractus | 0–11 | 0–1 | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–6 | 0–2 | ||
| saltgrass | DISP | Distichlis spicata | 0–6 | 0–1 | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–6 | 0–1 | ||
| low woollygrass | DAPU7 | Dasyochloa pulchella | 0–4 | 0–1 | ||
| giant dropseed | SPGI | Sporobolus giganteus | 0–2 | 0–1 | ||
|
Forb
|
||||||
| 2 | Forbs | 11–56 | ||||
| prickly Russian thistle | SATR12 | Salsola tragus | 0–84 | 0–25 | ||
| seepweed | SUAED | Suaeda | 0–45 | 0–5 | ||
| Forb, annual | 2FA | Forb, annual | 0–34 | 0–3 | ||
| Forb, perennial | 2FP | Forb, perennial | 0–34 | 0–3 | ||
| bastard toadflax | COUM | Comandra umbellata | 0–17 | 0–5 | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–11 | 0–2 | ||
| flatspine bur ragweed | AMAC2 | Ambrosia acanthicarpa | 7–11 | 0–2 | ||
| povertyweed | IVAX | Iva axillaris | 0–11 | 0–2 | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–9 | 0–3 | ||
| gooseberryleaf globemallow | SPGR2 | Sphaeralcea grossulariifolia | 0–9 | 0–1 | ||
| Pacific aster | SYCHC | Symphyotrichum chilense var. chilense | 0–6 | 0–2 | ||
| woolly plantain | PLPA2 | Plantago patagonica | 0–6 | 0–2 | ||
| flatspine stickseed | LAOC3 | Lappula occidentalis | 0–6 | 0–2 | ||
| rusty lupine | LUPU | Lupinus pusillus | 0–6 | 0–2 | ||
| James' buckwheat | ERJA | Eriogonum jamesii | 0–6 | 0–1 | ||
| Crescent milkvetch | ASAM5 | Astragalus amphioxys | 0–6 | 0–1 | ||
| skyblue phacelia | PHCO | Phacelia coerulea | 0–6 | 0–1 | ||
| tansymustard | DESCU | Descurainia | 0–3 | 0–5 | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–3 | 0–1 | ||
| saltlover | HAGL | Halogeton glomeratus | 0–3 | 0–1 | ||
| plains springparsley | CYAC | Cymopterus acaulis | 0–3 | 0–1 | ||
| pale evening primrose | OEPA | Oenothera pallida | 0–3 | 0–1 | ||
| Fremont cottonwood | POFR2 | Populus fremontii | 0–3 | – | ||
| snowball sand verbena | ABFR2 | Abronia fragrans | 0–2 | 0–1 | ||
| rayless tansyaster | MAGR2 | Machaeranthera grindelioides | 0–2 | 0–1 | ||
| tufted evening primrose | OECA10 | Oenothera caespitosa | 0–2 | 0–1 | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–1 | 0–1 | ||
| desert princesplume | STPI | Stanleya pinnata | 0–1 | 0–1 | ||
Table 23. Community 2.2 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 0 | Dominant Grasses | 336–785 | ||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 0–560 | 0–20 | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–560 | 0–20 | ||
| needle and thread | HECO26 | Hesperostipa comata | 0–224 | 0–15 | ||
| mesa dropseed | SPFL2 | Sporobolus flexuosus | 0–112 | 0–10 | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 45–90 | 0–5 | ||
| scarlet globemallow | SPCO | Sphaeralcea coccinea | 19–37 | – | ||
| 1 | 0–56 | |||||
| cheatgrass | BRTE | Bromus tectorum | 0–45 | 0–4 | ||
| James' galleta | PLJA | Pleuraphis jamesii | 0–45 | 0–4 | ||
| spike dropseed | SPCO4 | Sporobolus contractus | 0–11 | 0–1 | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–11 | 0–1 | ||
| blue grama | BOGR2 | Bouteloua gracilis | 0–6 | 0–1 | ||
| giant dropseed | SPGI | Sporobolus giganteus | 0–1 | 0–1 | ||
| contorted sphagnum | SPCO14 | Sphagnum contortum | 0–1 | 0–1 | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–1 | 0–1 | ||
| low woollygrass | DAPU7 | Dasyochloa pulchella | 0–1 | 0–1 | ||
| saltgrass | DISP | Distichlis spicata | 0–1 | 0–1 | ||
| squirreltail | ELEL5 | Elymus elymoides | 0–1 | 0–1 | ||
| needle and thread | HECO26 | Hesperostipa comata | 0–1 | 0–1 | ||
|
Forb
|
||||||
| 2 | Forbs | 11–56 | ||||
| prickly Russian thistle | SATR12 | Salsola tragus | 0–84 | 0–10 | ||
| seepweed | SUAED | Suaeda | 0–45 | 0–5 | ||
| Forb, annual | 2FA | Forb, annual | 0–37 | – | ||
| Forb, perennial | 2FP | Forb, perennial | 0–37 | – | ||
| bastard toadflax | COUM | Comandra umbellata | 0–17 | 0–5 | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–11 | 0–2 | ||
| povertyweed | IVAX | Iva axillaris | 0–11 | 0–2 | ||
| annual ragweed | AMAR2 | Ambrosia artemisiifolia | 7–11 | 0–2 | ||
| rayless tansyaster | MAGR2 | Machaeranthera grindelioides | 0–11 | 0–1 | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–9 | 0–3 | ||
| gooseberryleaf globemallow | SPGR2 | Sphaeralcea grossulariifolia | 0–9 | 0–1 | ||
| Crescent milkvetch | ASAM5 | Astragalus amphioxys | 0–6 | 0–3 | ||
| flatspine stickseed | LAOC3 | Lappula occidentalis | 0–6 | 0–2 | ||
| woolly plantain | PLPA2 | Plantago patagonica | 0–6 | 0–2 | ||
| rusty lupine | LUPU | Lupinus pusillus | 0–6 | 0–2 | ||
| Pacific aster | SYCHC | Symphyotrichum chilense var. chilense | 0–6 | 0–2 | ||
| skyblue phacelia | PHCO | Phacelia coerulea | 0–6 | 0–1 | ||
| James' buckwheat | ERJA | Eriogonum jamesii | 0–6 | 0–1 | ||
| curlycup gumweed | GRSQ | Grindelia squarrosa | 0–6 | 0–1 | ||
| tansymustard | DESCU | Descurainia | 0–3 | 0–5 | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–3 | 0–1 | ||
| plains springparsley | CYAC | Cymopterus acaulis | 0–3 | 0–1 | ||
| saltlover | HAGL | Halogeton glomeratus | 0–3 | 0–1 | ||
| pale evening primrose | OEPA | Oenothera pallida | 0–3 | 0–1 | ||
| tufted evening primrose | OECA10 | Oenothera caespitosa | 0–2 | 0–1 | ||
| snowball sand verbena | ABFR2 | Abronia fragrans | 0–2 | 0–1 | ||
| water hemlock | CICUT | Cicuta | 0–1 | 0–1 | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–1 | 0–1 | ||
| desert princesplume | STPI | Stanleya pinnata | 0–1 | 0–1 | ||
|
Shrub/Vine
|
||||||
| 3 | Shrubs | 28–112 | ||||
| rubber rabbitbrush | ERNAN5 | Ericameria nauseosa ssp. nauseosa var. nauseosa | 0–101 | 0–8 | ||
| fourwing saltbush | ATCA2 | Atriplex canescens | 0–45 | 0–4 | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–28 | 0–1 | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–11 | 0–2 | ||
| greasewood | SAVE4 | Sarcobatus vermiculatus | 0–11 | 0–1 | ||
| desert pepperweed | LEFR2 | Lepidium fremontii | 0–6 | 0–2 | ||
| shadscale saltbush | ATCO | Atriplex confertifolia | 0–6 | 0–2 | ||
| sand sagebrush | ARFI2 | Artemisia filifolia | 0–6 | 0–1 | ||
| Stansbury cliffrose | PUST | Purshia stansburiana | 0–2 | 0–1 | ||
| basin big sagebrush | ARTRT | Artemisia tridentata ssp. tridentata | 0–1 | 0–1 | ||
Table 24. Community 2.3 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | Grass | 56–112 | ||||
| Indian ricegrass | ACHY | Achnatherum hymenoides | 6–84 | 1–7 | ||
| cheatgrass | BRTE | Bromus tectorum | 3–45 | 1–4 | ||
| spike dropseed | SPCO4 | Sporobolus contractus | 0–45 | 0–4 | ||
| sand dropseed | SPCR | Sporobolus cryptandrus | 0–28 | 0–3 | ||
| squirreltail | ELEL5 | Elymus elymoides | 0–11 | 0–5 | ||
| James' galleta | PLJA | Pleuraphis jamesii | 0–11 | 0–1 | ||
| contorted sphagnum | SPCO14 | Sphagnum contortum | 0–11 | 0–1 | ||
| saltgrass | DISP | Distichlis spicata | 0–6 | 0–2 | ||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–6 | 0–2 | ||
| needle and thread | HECO26 | Hesperostipa comata | 0–6 | 0–2 | ||
| mesa dropseed | SPFL2 | Sporobolus flexuosus | 0–6 | 0–2 | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–6 | 0–2 | ||
| low woollygrass | DAPU7 | Dasyochloa pulchella | 0–4 | 0–2 | ||
| giant dropseed | SPGI | Sporobolus giganteus | 0–2 | 0–1 | ||
|
Forb
|
||||||
| 2 | Forbs | 28–140 | ||||
| prickly Russian thistle | SATR12 | Salsola tragus | 11–140 | 0–12 | ||
| seepweed | SUAED | Suaeda | 0–45 | 0–5 | ||
| Forb, annual | 2FA | Forb, annual | 0–34 | 0–3 | ||
| Forb, perennial | 2FP | Forb, perennial | 0–34 | 0–3 | ||
| bastard toadflax | COUM | Comandra umbellata | 0–17 | 0–2 | ||
| povertyweed | IVAX | Iva axillaris | 0–11 | 0–5 | ||
| Brenda's yellow cryptantha | CRFL5 | Cryptantha flava | 0–11 | 0–1 | ||
| flatspine bur ragweed | AMAC2 | Ambrosia acanthicarpa | 0–11 | 0–1 | ||
| Fendler's sandmat | CHFE3 | Chamaesyce fendleri | 0–9 | 0–1 | ||
| gooseberryleaf globemallow | SPGR2 | Sphaeralcea grossulariifolia | 0–9 | 0–1 | ||
| Pacific aster | SYCHC | Symphyotrichum chilense var. chilense | 0–6 | 0–2 | ||
| rusty lupine | LUPU | Lupinus pusillus | 0–6 | 0–2 | ||
| woolly plantain | PLPA2 | Plantago patagonica | 0–6 | 0–2 | ||
| flatspine stickseed | LAOC3 | Lappula occidentalis | 0–6 | 0–2 | ||
| James' buckwheat | ERJA | Eriogonum jamesii | 0–6 | 0–1 | ||
| Crescent milkvetch | ASAM5 | Astragalus amphioxys | 0–6 | 0–1 | ||
| skyblue phacelia | PHCO | Phacelia coerulea | 0–6 | 0–1 | ||
| tansymustard | DESCU | Descurainia | 0–3 | 0–5 | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–3 | 0–1 | ||
| plains springparsley | CYAC | Cymopterus acaulis | 0–3 | 0–1 | ||
| saltlover | HAGL | Halogeton glomeratus | 0–3 | 0–1 | ||
| pale evening primrose | OEPA | Oenothera pallida | 0–3 | 0–1 | ||
| hoary tansyaster | MACA2 | Machaeranthera canescens | 0–2 | 0–1 | ||
| tufted evening primrose | OECA10 | Oenothera caespitosa | 0–2 | 0–1 | ||
| snowball sand verbena | ABFR2 | Abronia fragrans | 0–2 | 0–1 | ||
| water hemlock | CICUT | Cicuta | 0–1 | 0–1 | ||
| Jones' pepperweed | LEMOJ | Lepidium montanum var. jonesii | 0–1 | 0–1 | ||
| desert princesplume | STPI | Stanleya pinnata | 0–1 | 0–1 | ||
|
Shrub/Vine
|
||||||
| 3 | Shrubs | 168–280 | ||||
| fourwing saltbush | ATCA2 | Atriplex canescens | 112–252 | 10–20 | ||
| rubber rabbitbrush | ERNA10 | Ericameria nauseosa | 0–78 | 0–3 | ||
| broom snakeweed | GUSA2 | Gutierrezia sarothrae | 0–45 | 0–4 | ||
| desert pepperweed | LEFR2 | Lepidium fremontii | 0–45 | 0–2 | ||
| Shrub (>.5m) | 2SHRUB | Shrub (>.5m) | 0–34 | 0–3 | ||
| shadscale saltbush | ATCO | Atriplex confertifolia | 0–28 | 0–3 | ||
| sand sagebrush | ARFI2 | Artemisia filifolia | 0–17 | 0–2 | ||
| basin big sagebrush | ARTRT | Artemisia tridentata ssp. tridentata | 0–17 | 0–2 | ||
| plains pricklypear | OPPO | Opuntia polyacantha | 0–11 | 0–2 | ||
| winterfat | KRLA2 | Krascheninnikovia lanata | 0–7 | 0–3 | ||
Table 25. Community 3.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) |
|---|
Interpretations
Animal community
--Wildlife Interpretation--
Herds of mule deer, pronghorn antelope, and elk can be seen grazing/browsing on these sites, especially when near water sources and in the winter. The hot climate favors small mammals, which have an easier time finding shelter, food, and water. Many species of rats, mice, squirrels, bats, and chipmunks can be observed, along with coyotes and foxes. Lizards are the most visible and can be observed during the day. Species may include the northern whiptail, desert spiny, and the colorful western collard lizard. (NPS.gov, 2008)
--Grazing Interpretations--
This site provides good spring, fall, and winter grazing conditions for livestock due to accessibility and available nutritious forage. Yet, this site may lack natural perennial water sources, which can influence the suitability for livestock grazing. Perennial grasses provide good spring and fall grazing conditions for all classes of livestock. Shrubs, including fourwing saltbush, Cutler jointfir, and winterfat and provide good winter browse for cattle, sheep, and goats. Cutler jointfir is typically only browsed by livestock in the fall and winter due to poor nutritional value in the spring and summer. Forb composition and annual production depends primarily on precipitation amounts and thus is challenging to use in livestock grazing management decisions. However, forb composition should be monitored for species diversity, as well as poisonous or injurious plant communities which may be detrimental to livestock if grazed. Before making specific grazing management recommendations, an onsite evaluation must be made.
Recreational uses
Recreation activities include aesthetic value and good opportunities for hiking, horseback riding, hunting, and off-road vehicle use. Camping sites are usually limited due to lack of sheltering trees or rock outcrop.
Wood products
None
Other information
--Poisonous/Toxic Plant Species--
Toxic plants associated with this site include woolly locoweed, broom snakeweed, and sand sagebrush. Woolly locoweed is toxic to all classes of livestock and wildlife. This plant is palatable and has similar nutrient value to alfalfa, which may cause animals to consume it even when other forage is unavailable. Many locoweed species contain swainsonine (indolizdine alkaloid) and are 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 stage. Cattle and sheep will generally graze broom snakeweed when other forage is unavailable, typically in winter when toxicity levels are at their lowest. Sand sagebrush is toxic to horses, but not to other livestock and wildlife ruminants. This plant contains sesquiterpene lactones and monoterpenes, where toxic concentrations are greatest in the late fall and winter. Horses develop neurological signs and exhibit abnormal behavior, such as ataxia and the tendency to fall down, after eating sand sagebrush for several days. (Knight and Walter, 2001)
Russian thistle is an invasive toxic plant, causing nitrate and to a lesser extent oxalate poisoning, which affects all classes of livestock. The buildup of nitrates in these plants is highly dependent upon environmental factors, such as after a rain storm during a drought, cool/cloudy days, and soils high in nitrogen and low in sulfur and phosphorus, all which cause increased nitrate accumulation. Nitrate collects in the stems and can persist throughout the growing season. Clinical signs of nitrate poisoning include drowsiness, weakness, muscular tremors, increased heart and respiratory rates, staggering gait, and death. Conversely, oxalate poisoning causes kidney failure; clinical signs include muscle tremors, tetany, weakness, and depression. Poisoning generally occurs when livestock consume and are not accustomed to grazing oxalate-containing plants. Animals with prior exposure to oxalates have increased numbers of oxalate-degrading rumen microflora and thus are able to degrade the toxin before clinical poisoning can occur. (Knight and Walter, 2001)
--Invasive Plant Communities--
Generally, as ecological conditions deteriorate and perennial vegetation decreases due to disturbance (fire, over grazing, drought, off road vehicle overuse, erosion, etc.) undesirable plants will invade the site. Of particular concern on this site are cheatgrass, Russian thistle, 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 possible.
Cheatgrass and Russian thistle are common invaders to this site, especially in lower areas that concentrate nutrients and moisture. In some cases cheatgrass has been able to establish into an intact perennial grass and shrub community, but disturbed communities are more susceptible to invasion and domination by invasive plant species. If growing conditions are conducive to invaders and the disturbance is not removed, these plants can create monotypic stands that can alter the nutrient cycling, erosion rates and the fire regime of the area.
Supporting information
Other references
Howard, Janet L. 2003. Atriplex canescens. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/ [2012, August 20]..
Contributors
George Cook
Jamin Johanson
Susanne Mayne
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) | Shane A. Green (NRCS), Robert D. Stager (BLM), Dana Truman (NRCS), Paul Curtis (BLM) and Randy Beckstrand (BLM) |
|---|---|
| Contact for lead author | shane.green@ut.usda.gov |
| Date | 09/10/2008 |
| Approved by | Shane A. Green |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
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Number and extent of rills:
Very minor rill development, increasing as slope steepens. Rill development will increase following large storm events, but rills heal within a few months due to the very sandy soil textures on soils that have weak soil structure. -
Presence of water flow patterns:
Flow patterns will occur more often on soils with more structure (fine sandy loams), and less often on soils with less structure (sands). Flow patterns are usually sinuous and wind around perennial plant bases and show very minor evidence of erosion due to sandy texture of soil. They are expected to be short (3 to 6 feet), narrow (less than 1 foot), and somewhat widely spaced (> 15 feet). They are typically stable with only minor evidence of deposition. Evidence of flow will increase somewhat with a slope greater than 3 percent. This site is periodically inundated with runoff water (i.e. in flash floods) due to its geomorphic location.
During very high flow events in adjacent channels (lotic, wash, etc.), this site may act as a filter and trap sediment, sometimes up to a foot or more.
-
Number and height of erosional pedestals or terracettes:
Plants may show very minor pedestalling where they are adjacent to water flow patterns, but there should never be any exposed roots. Terracettes should be very few and stable, occurring behind pieces of woody litter blocking water flow patterns. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
30-45%. Ground cover is based on the first raindrop impact, and bare ground is the opposite of ground cover. Ground cover + bare ground = 100%. 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. -
Number of gullies and erosion associated with gullies:
Very few. They would usually be expected in the lowest part of the site where water flows concentrate and/or in locations where there are concentrated flows into the site from an adjacent area. Gullies may show minor signs of active erosion but the sides and bottoms would be mostly stabilized with perennial vegetation. Gullies may show more indication of erosion on slopes greater than 3 percent, or as influenced by adjacent areas (watersheds) that may be providing concentrated flow patterns. -
Extent of wind scoured, blowouts and/or depositional areas:
Slight wind generated soil movement is normal. Wind caused blowouts and deposition are rare. If present, they are mostly stable or have healed over. Coppice mounding around perennial vegetation may occur is typical. -
Amount of litter movement (describe size and distance expected to travel):
Due to the natural periodic concentration of runoff in this site, some fine litter movement is common. Often litter from adjacent sites/watershed contribute to litter noted on this ecological site. Litter removal may occur in flow patterns with deposition occurring at points of obstruction, especially following large storm events. Litter movement is expected to increase with slopes over 3 percent. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
This site should have a soil stability rating of 4 or 5 under the plant canopies and a rating of 3 to 4 in the interspaces using the soil stability kit test. The average should be a 4. Surface texture is loamy sand to sandy loam. Vegetation cover, litter, and surface rock reduce erosion. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Soil surface horizon is typically 3 to 6 inches deep. Structure is typically moderate fine granular. Color is typically light brown (7.5YR6/4) to light brownish gray (10YR6/2). 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:
Vascular plants are expected to break raindrop impact and splash erosion. Spatial distribution of vascular plants slows runoff by obstructing surface flows to help create sinuous flow patterns that dissipate energy and allow time for infiltration within the naturally receptive loamy sand to sandy loam soil textures. With the geomorphic location of the site being in low stream terraces, flood plains, alluvial bottoms, channels and valley flats, and alluvial fans this site is one of the terminal accumulation sites for runoff water. As such, infiltration is naturally facilitated. Natural erosion would be expected in severe thunder storms or heavy spring runoff. When perennial grasses decrease, reducing ground cover and increasing bare ground, runoff is expected to increase and any associated infiltration reduced. -
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:
Perennial bunchgrasses (Indian ricegrass, Galleta, Sand dropseed) > non-sprouting shrubs (Fourwing saltbush)Sub-dominant:
perennial and native annual forbs (Globemallow and others) > sprouting shrubs (Torrey tea, rabbitbrush, Sand sagebrush)Other:
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, Smooth brome, Intermediate wheatgrass, etc.)
Biological soil crust is variable in its expression where present on this site and is measured as a component of ground cover.
Forbs can be expected to vary widely in their expression in the plant community based upon departures from average growing conditions.
Additional:
Assumed disturbance regime includes insects, very infrequent fire, and flooding that kills the non-sprouting shrub species. Dominance by average annual production:
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 reflect a community phase within the reference state.
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
During years with average to above average precipitation, there should be very little recent mortality or decadence apparent in either the shrubs or grasses. Some mortality of bunchgrass and other shrubs may occur during very severe (long term) droughts. Snakeweed may normally die out on 7-10 year cycles. -
Average percent litter cover (%) and depth ( in):
Litter cover (including under plants) nearly all of which should be fine litter. Depth should be 1-2 leaf thickness in the interspaces and up to 1/2” under canopies. Litter cover may increase to 15-20% on some years due to increased plant production. -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
550-650 #/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:
Cheatgrass, filaree, other annual forbs, common ragweed, Russian thistle and common sunflower. -
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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