Natural Resources
Conservation Service
Ecological site R070CY122NM
Shallow Sandy Savanna
Last updated: 10/21/2024
Accessed: 11/23/2024
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): 042C–Central New Mexico Highlands
Major Land Resource Area (MLRA): 070C–Central New Mexico Highlands
Major Land Resource Area (MLRA) 70C - will become 42C - is a high elevation portion of central New Mexico that is the convergence of four major physiographic provinces: Basin and Range, Southern Rocky Mountains, Great Plains, and Colorado Plateau. As such, it contains parts or characteristics of each, though tectonically, as a region, it is the easternmost extent of the Basin and Range Province and, more specifically, a structural expression of the Rio Grande Rift. It consists mostly of rangeland with some forested areas associated with numerous disconnected mountain ranges such as the Guadalupe, Sacramento, and Manzano Mountains. Other major physiographic features include the Galisteo Basin or the enclosed Estancia Basin, the structural Chupadera and Glorieta Mesas, and the piedmonts of the Buchanan and Guadalupe Mesas.
Ecological site concept
This site occurs on nearly level to moderately sloping side slopes of foothills and on tops of hills and mesas. Slopes range from 3 to 25 percent but are usually less than 10 percent.
The soils of this site are well drained and shallow to very shallow over petrocalcic material (caliche) or sandstone. The surface texture is fine sandy loam.
Table 1. Dominant plant species
Tree |
(1) Juniperus |
---|---|
Shrub |
(1) Rhus trilobata |
Herbaceous |
(1) Schizachyrium scoparium |
Physiographic features
This site occurs on nearly level to moderately sloping side slopes of foothills and on tops of hills and mesas. Typically, this site grades down from the steep slopes of physiographic breaks. Slopes range from 3 to 25 percent but are usually less than 10 percent. Direction of slope varies and is usually not significant. Elevations range from 4,500 to 7,000 feet above sea level.
Table 2. Representative physiographic features
Landforms |
(1)
Hill
(2) Mesa |
---|---|
Elevation | 1,372 – 2,134 m |
Slope | 3 – 25% |
Aspect | Aspect is not a significant factor |
Climatic features
The climate of the area is “semi-arid continental.”
The average annual precipitation ranges from 13 to 16 inches. Variations of 5 inches, more or less, are common. Seventy-five percent of the precipitation falls from April to October. Most of the summer precipitation falls in the form of high-intensity, short-duration thunderstorms.
Distinct seasonal changes and large annual and diurnal temperature changes characterize temperatures. The average annual temperature is about 50 degrees F with extremes of -29 degrees F in the winter and 103 degrees F in the summer.
The average frost-free season is 130 to 160 days. The last killing frost falling in early May and the first killing frost in early October.
Both temperature and precipitation favor warm-season, perennial plant species. However, about 40 percent of the precipitation falls at a time favorable for cool-season plant growth. This allows the cool-season species to occupy a very important component in this plant community. Vegetation responds well to light rains due to the shallow soil depth and soil surface textures. Heavy rains produce excess runoff and can cause flash floods. Strong winds from the west and southwest blow across the area from February to June and dries the soil during a critical period for plant growth.
Climate data was obtained from http://www.wrcc.sage.dri.edu/summary/climsmnm.html web site using 50% probability for freeze-free and frost-free seasons using 28.5 degrees F and 32.5 degrees F respectively.
Table 3. Representative climatic features
Frost-free period (average) | 173 days |
---|---|
Freeze-free period (average) | 187 days |
Precipitation total (average) | 406 mm |
Figure 2. Monthly precipitation range
Figure 3. Monthly average minimum and maximum temperature
Influencing water features
This is an upland site, and is not associated with water features or wetlands. During heavy rain events, this site may receive run-on moisture from landforms above and contribute runoff to landforms below.
Soil features
The soils of this site are well drained and shallow to very shallow over petrocalcic material (caliche) or sandstone. The surface texture is fine sandy loam. This extends to a depth of 12 to 20 inches. The root-restrictive layer is encountered at 12 to 20 inches. Permeability is rapid and water-holding capacity is medium.
Table 4. Representative soil features
Surface texture |
(1) Fine sandy loam |
---|---|
Family particle size |
(1) Clayey |
Drainage class | Well drained |
Permeability class | Very slow to slow |
Soil depth | 10 – 51 cm |
Available water capacity (0-101.6cm) |
15.24 – 22.86 cm |
Soil reaction (1:1 water) (0-101.6cm) |
6.6 – 8.4 |
Subsurface fragment volume <=3" (Depth not specified) |
5 – 14% |
Subsurface fragment volume >3" (Depth not specified) |
2% |
Ecological dynamics
Continuous grazing of this site during the growing season will cause the high producing desirable forage plants such as little bluestem, sideoats grama, black grama, bottlebrush squirreltail, prairie junegrass, littleseed ricegrass and sumac to decrease. This will be followed by an increase in blue grama, threeawns, ring muhly, juniper, oak, algerita, and cholla. As the condition of this site deteriorates, a sharp increase in juniper will occur. As the tree canopy increases, the understory vegetation will sharply decrease. The increased numbers of trees may be attributed partly to the control of fire. Brush management is needed once the canopy exceeds 25 percent. Mechanical control is not feasible due to the shallow and sandy nature of the soils. A system of grazing that varies the season of use is most beneficial to maintain or improve the plant community.
State and transition model
Figure 4. Generalized STM for shallow soils in 70C
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Ecosystem states
State 1 submodel, plant communities
State 1
Reference State
This state represents the most ecologically stable conditions in terms of resistance to erosion. Moreover, this state has the highest potential for productivity and plant diversity.
Community 1.1
Reference Plant Community
This phase has an open stand of pinyon pine and/or juniper with grass understory. The understory grasses are characterized by both warm and cool-season, mid-grasses with scattered shrubs throughout. Half-shrubs and forbs are a minor part of the plant community. The open stand of pinyon and juniper at one time may have been maintained by natural fire. The tree canopy cover ranges from 10 to 25 percent. Other grasses that could appear on this phase include: hairy grama, needleandthread, New Mexico feathergrass, big bluestem, western wheatgrass, pinyon ricegrass, spike muhly, mountain muhly, Metcalfe muhly, curlyleaf muhly, silver bluestem, mat muhly, alkali sacaton, pine dropseed, sedges, and Indian ricegrass. Other woody plants include: rubber rabbitbrush, Bigelow sagebrush, winterfat, pricklypear, fourwing saltbush, sand sagebrush, threadleaf groundsel, broom snakeweed, yucca, sacahuista, ponderosa pine and mountainmahogany.
Figure 5. 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 | 247 | 628 | 1009 |
Forb | 22 | 67 | 112 |
Total | 269 | 695 | 1121 |
Table 6. Ground cover
Tree foliar cover | 10-25% |
---|---|
Shrub/vine/liana foliar cover | 2-5% |
Grass/grasslike foliar cover | 0% |
Forb foliar cover | 0% |
Non-vascular plants | 0% |
Biological crusts | 0% |
Litter | 5-10% |
Surface fragments >0.25" and <=3" | 0% |
Surface fragments >3" | 0% |
Bedrock | 0% |
Water | 0% |
Bare ground | 20-50% |
Figure 6. Plant community growth curve (percent production by month). NM4322, R070CY122NM Shallow Sandy Savanna Reference State. R070CY122NM Shallow Sandy Savanna Reference State Open stand of pinyon/juniper w/ mixed warm/cool-season mid-grasses w/ scattered shrubs..
Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|
J | F | M | A | M | J | J | A | S | O | N | D |
0 | 0 | 5 | 7 | 10 | 15 | 25 | 25 | 8 | 5 | 0 | 0 |
State 2
Degraded
This state is characterized by increased amounts of blue grama, threeawns, ring muhly, juniper, oak, algerita, and cholla. As the condition of this site deteriorates, a sharp increase in juniper will occur.
Transition T1A
State 1 to 2
Season-long grazing providing little rest and recovery for preferred grazed plants during critical growing periods, coupled with high utilization.
Restoration pathway R2A
State 2 to 1
Legacy text: "Restoration pathway resulting from the implementation of prescribed grazing." It should be noted that prescribed grazing alone may not effectively diminish woody plants here. Brush control may also be required. Future work on this ESD should seek to clarify this.
Conservation practices
Grazing Management Plan - Applied |
---|
Additional community tables
Table 7. Community 1.1 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (kg/hectare) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | 123–168 | |||||
little bluestem | SCSC | Schizachyrium scoparium | 127–168 | – | ||
2 | 123–168 | |||||
sideoats grama | BOCU | Bouteloua curtipendula | 127–168 | – | ||
3 | 45–123 | |||||
black grama | BOER4 | Bouteloua eriopoda | 43–127 | – | ||
4 | 45–123 | |||||
blue grama | BOGR2 | Bouteloua gracilis | 43–127 | – | ||
James' galleta | PLJA | Pleuraphis jamesii | 43–127 | – | ||
5 | 45–78 | |||||
squirreltail | ELEL5 | Elymus elymoides | 43–84 | – | ||
6 | 45–78 | |||||
plains lovegrass | ERIN | Eragrostis intermedia | 43–84 | – | ||
7 | 22–45 | |||||
prairie Junegrass | KOMA | Koeleria macrantha | 26–43 | – | ||
8 | 22–45 | |||||
common wolfstail | LYPH | Lycurus phleoides | 26–43 | – | ||
9 | 45–78 | |||||
sand dropseed | SPCR | Sporobolus cryptandrus | 43–84 | – | ||
10 | 45–67 | |||||
pinyon ricegrass | PIFI | Piptochaetium fimbriatum | 43–67 | – | ||
11 | 22–45 | |||||
threeawn | ARIST | Aristida | 26–43 | – | ||
12 | 22–45 | |||||
ring muhly | MUTO2 | Muhlenbergia torreyi | 26–43 | – | ||
13 | 45–78 | |||||
Graminoid (grass or grass-like) | 2GRAM | Graminoid (grass or grass-like) | 43–84 | – | ||
Forb
|
||||||
14 | 22 | |||||
buckwheat | ERIOG | Eriogonum | 26–43 | – | ||
15 | 22–45 | |||||
scarlet globemallow | SPCO | Sphaeralcea coccinea | 26–43 | – | ||
16 | 22–45 | |||||
golden Indian paintbrush | CALE27 | Castilleja levisecta | 26–43 | – | ||
17 | 22–45 | |||||
woolly plantain | PLPA2 | Plantago patagonica | 26–43 | – | ||
18 | 22–45 | |||||
Forb (herbaceous, not grass nor grass-like) | 2FORB | Forb (herbaceous, not grass nor grass-like) | 26–43 | – | ||
Tree
|
||||||
19 | 78–213 | |||||
juniper | JUNIP | Juniperus | 84–211 | – | ||
twoneedle pinyon | PIED | Pinus edulis | 84–211 | – | ||
Shrub/Vine
|
||||||
20 | 22–45 | |||||
skunkbush sumac | RHTR | Rhus trilobata | 26–43 | – | ||
21 | 22–45 | |||||
algerita | MATR3 | Mahonia trifoliolata | 26–43 | – | ||
22 | 22–45 | |||||
oak | QUERC | Quercus | 26–43 | – | ||
23 | 22–45 | |||||
pricklypear | OPUNT | Opuntia | 26–43 | – | ||
24 | 22–45 | |||||
prairie sagewort | ARFR4 | Artemisia frigida | 26–43 | – | ||
prairie sagewort | ARFR4 | Artemisia frigida | 26–43 | – | ||
25 | 22–45 | |||||
Shrub, deciduous | 2SD | Shrub, deciduous | 26–43 | – | ||
Shrub, deciduous | 2SD | Shrub, deciduous | 26–43 | – |
Interpretations
Supporting information
Type locality
Location 1: Chaves County, NM | |
---|---|
Location 2: Lincoln County, NM | |
Location 3: San Miguel County, NM | |
Location 4: Santa Fe County, NM | |
Location 5: Torrance County, NM |
Other references
Data collection for this site was done in conjunction with the progressive soil surveys within the Pecos-Canadian Plains and Valleys 70 Major Land Resource Area of New Mexico. This site has been mapped and correlated with soils in the following soil surveys: Chaves, De Baca, Guadalupe, Lincoln, Sna Miguel, Santa Fe, Torrance.
Characteristic Soils Are:
Bond, Plack
Other Soils included are:
Dean(as mapped in San Miguel County) Sombordoro(as mapped in San Miguel County)
Contributors
Christine Bishop
Don Sylvester
Elizabeth Wright
John Tunberg
Approval
Kendra Moseley, 10/21/2024
Rangeland health reference sheet
Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.
Author(s)/participant(s) | |
---|---|
Contact for lead author | |
Date | 11/23/2024 |
Approved by | Kendra Moseley |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
-
Presence of water flow patterns:
-
Number and height of erosional pedestals or terracettes:
-
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
-
Number of gullies and erosion associated with gullies:
-
Extent of wind scoured, blowouts and/or depositional areas:
-
Amount of litter movement (describe size and distance expected to travel):
-
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
-
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
-
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
-
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
-
Functional/Structural Groups (list in order of descending dominance by above-ground annual-production or live foliar cover using symbols: >>, >, = to indicate much greater than, greater than, and equal to):
Dominant:
Sub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
-
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
-
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:
-
Perennial plant reproductive capability:
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