Natural Resources
Conservation Service
Ecological site R040XB222AZ
Volcanic Hills 7"-10" p.z.
Accessed: 12/22/2024
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): 040X–Sonoran Basin and Range
AZ 40.2 – Middle Sonoran Desert
Elevations range from 1200 to 2000 feet and precipitation averages 7 to 10 inches per year. Vegetation includes saguaro, palo verde, creosotebush, triangle bursage, brittlebush, prickly pear, cholla, desert saltbush, wolfberry bush muhly, threeawns, and big galleta. The soil temperature regime is hyperthermic and the soil moisture regime is typic aridic. This unit occurs within the Basin and Range Physiographic Province and is characterized by numerous mountain ranges that rise abruptly from broad, plain-like valleys and basins. Igneous and metamorphic rock classes dominate the mountain ranges and sediments filling the basins represent combinations of fluvial, lacustrine, colluvial and alluvial deposits.
Table 1. Dominant plant species
| Tree |
(1) Parkinsonia microphylla |
|---|---|
| Shrub |
(1) Ambrosia deltoidea |
| Herbaceous |
(1) Muhlenbergia porteri |
Physiographic features
This site occurs on hillslopes and ridgetops. Slopes range from 15% to 65%. Elevations are from 1000 to 2500 feet. Slope aspect is site differentiating at elevations near land resource area boundaries.
Table 2. Representative physiographic features
| Landforms |
(1)
Hill
(2) Ridge |
|---|---|
| Elevation | 1,000 – 2,500 ft |
| Slope | 15 – 65% |
Climatic features
Precipitation in the sub-resource area ranges from 7 to 10 inches. Elevations range from 900 to 2050 feet. Winter-summer rainfall ratios range from 40% to 60% in the southern part along the international boundary, to 60% to 40% in the central and northern parts of the sub-resource area. As one moves from east to west in this resource area rains become more unpredictable and variable with Coefficients of Variation of annual rainfall equal to 38% at Florence and 46% at Aguila. Summer rains fall July- September, originate in the Gulf of Mexico, and are convective, usually brief, intense thunderstorms. Summer precipitation is extremely erratic and undependable in this area. Cool season moisture tends to be frontal, originates in the Pacific and Gulf of California, and falls in widespread storms with long duration and low intensity. This is the dependable moisture supply for vegetation in the area. Snow is very rare and usually melts on contact. May-June is the driest time of the year. Humidity is very low.
Winter temperatures are very mild with very few days recording freezing for short periods of time. Summertime temperatures are hot to very hot with many days in June-July exceeding 105 degrees F. Frost-free days range from 280 at stations in major river valleys with cold air drainage to 320 to 350 days at upland stations.
Both the spring and the summer growing seasons are equally important for perennial grass, forb and shrub growth. Cool and warm season annual forbs and grasses can be common in their respective seasons with above average rainfall. Perennial forage species can remain green throughout the year with available moisture.
Table 3. Representative climatic features
| Frost-free period (average) | 350 days |
|---|---|
| Freeze-free period (average) | 0 days |
| Precipitation total (average) | 10 in |
Figure 2. Monthly precipitation range
Figure 3. Monthly average minimum and maximum temperature
Influencing water features
Soil features
These are shallow soils formed on intermediate igneous parent materials; andesite, dacite, diorite, and on shale. Parent material kind includes slope alluvium. Parent material origin includes rhyolite. Surface texture modifier includes very cobbly and stony. Bedrock is usually hard and unweathered. They are slightly calcareous, loamy textured and have very well developed covers of cobble, stones, and gravel. Numerous areas of rock outcrop occur intermingled with soil areas. Outcrops can be as high as 35% of the area. Plant-soil moisture relationships are fair to good.
Soils mapped on this site include: SSA-645 Aguila-Carefree area MU's Gachado(STV phase) > 15% slopes-51, 52 & 103, Lomitas-52; SSA-661 Eastern Pinal-Southern Gila counties MU's Gachado(STV phase) > 15% slopes-610 & Lomitas-610.
Table 4. Representative soil features
| Parent material |
(1)
Slope alluvium
–
andesite
|
|---|---|
| Surface texture |
(1) Very gravelly sandy loam (2) Extremely gravelly loam (3) Cobbly |
| Family particle size |
(1) Loamy |
| Drainage class | Well drained |
| Permeability class | Moderately rapid |
| Soil depth | 4 – 20 in |
| Surface fragment cover <=3" | 35 – 65% |
| Surface fragment cover >3" | 1 – 15% |
| Available water capacity (0-40in) |
0.2 – 1.6 in |
| Calcium carbonate equivalent (0-40in) |
2 – 10% |
| Electrical conductivity (0-40in) |
Not specified |
| Sodium adsorption ratio (0-40in) |
Not specified |
| Soil reaction (1:1 water) (0-40in) |
7.9 – 8.4 |
| Subsurface fragment volume <=3" (Depth not specified) |
35 – 65% |
| Subsurface fragment volume >3" (Depth not specified) |
1 – 15% |
Ecological dynamics
The plant communities found on an ecological site are naturally variable. Composition and production will vary with yearly conditions, location, aspect, and the natural variability of the soils. The Historical Climax Plant Community represents the natural potential plant communities found on relict or relatively undisturbed sites. Other plant communities described here represent plant communities that are known to occur when the site is disturbed by factors such as fire, grazing, or drought.
Production data provided in this site description is standardized to air dry weight at the end of the summer growing season. The plant communities described in this site description are based on near normal rainfall years.
NRCS uses a Similarity Index to compare existing plant communities to the plant communities described here. Similarity Index is determined by comparing the production and composition of a plant community to the production and composition of a plant community described in this site description. To determine Similarity Index, compare the production (air dry weight) of each species to that shown in the plant community description. For each species, count no more than the maximum amount shown for the species, and for each group, count no more than the maximum amount shown for the group. Divide the resulting total by the total normal year production shown in the plant community description. If the rainfall has been significantly above or below normal, use the total production shown for above or below normal years. If field data is not collected at the end of the summer growing season, then the field data must be corrected to the end of the year production before comparing it to the site description. The growth curve can be used as a guide for estimating production at the end of the summer growing season.
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 1
Historical Climax Plant Community
Community 1.1
Historical Climax Plant Community
The potential plant community is a diverse mixture of desert shrubs, trees and cacti. The aspect is shrubland. Continuous, heavy grazing removes the small percentage of perennial grass and forbs from the plant community. Cobble and gravel covers are continuous and average 95%. Basal cover of perennial plants is about 2% and bare ground averages 3%. Dark colored surface fragments warm the soil allowing plants to grow in late winter. Cryptogam (moss) cover is lacking or very low and lichens on stones is low even on north aspects. Plant populations of major species are 1000 to 1500 plants per acre for triangle bursage, 20 to 50 trees per acre for paloverde, about 200 per acre for creosotebush, 100 to 150 per acre for wolfberry, 10 to 60 saguaros per acre, about 300 plants per acre for cholla species and 1 to 20 ocotillo per acre. In the northern part of this land resource area, introduced cool season annual grasses like red brome and schismus have invaded native plant communities and have reduced production of native shrubs significantly. Teddy bear cholla predominates on south aspects and buckhorn cholla on north aspects. In some areas basalt flows capping acid igneous parent materials produces a site having the appearance of Basalt Hills, but the plant community is better described by this Volcanic Hills range site description.
Figure 4. 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 | 400 | – | 450 |
| Forb | 25 | – | 75 |
| Grass/Grasslike | 25 | – | 50 |
| Total | 450 | – | 575 |
Additional community tables
Table 6. Community 1.1 plant community composition
| Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/Grasslike
|
||||||
| 1 | 10–25 | |||||
| slim tridens | TRMU | Tridens muticus | 0–3 | – | ||
| bush muhly | MUPO2 | Muhlenbergia porteri | 0–3 | – | ||
| tobosagrass | PLMU3 | Pleuraphis mutica | 0–2 | – | ||
| big galleta | PLRI3 | Pleuraphis rigida | 0–2 | – | ||
| Parish's threeawn | ARPUP5 | Aristida purpurea var. parishii | 0–2 | – | ||
| slender grama | BORE2 | Bouteloua repens | 0–2 | – | ||
| red grama | BOTR2 | Bouteloua trifida | 0–2 | – | ||
| curly-mesquite | HIBE | Hilaria belangeri | 0–2 | – | ||
| purple threeawn | ARPU9 | Aristida purpurea | 0–2 | – | ||
| Fendler's threeawn | ARPUF | Aristida purpurea var. fendleriana | 0–1 | – | ||
| blue threeawn | ARPUN | Aristida purpurea var. nealleyi | 0–1 | – | ||
| desert needlegrass | ACSP12 | Achnatherum speciosum | 0–1 | – | ||
| low woollygrass | DAPU7 | Dasyochloa pulchella | 0–1 | – | ||
| Arizona cottontop | DICA8 | Digitaria californica | 0–1 | – | ||
| nineawn pappusgrass | ENDE | Enneapogon desvauxii | 0–1 | – | ||
| tanglehead | HECO10 | Heteropogon contortus | 0–1 | – | ||
| Wright's threeawn | ARPUW | Aristida purpurea var. wrightii | 0–1 | – | ||
| spidergrass | ARTE3 | Aristida ternipes | 0–1 | – | ||
| spidergrass | ARTEG | Aristida ternipes var. gentilis | 0–1 | – | ||
| sideoats grama | BOCU | Bouteloua curtipendula | 0–1 | – | ||
| 2 | 5–25 | |||||
| sixweeks fescue | VUOC | Vulpia octoflora | 0–5 | – | ||
| sixweeks threeawn | ARAD | Aristida adscensionis | 0–5 | – | ||
| prairie threeawn | AROL | Aristida oligantha | 0–5 | – | ||
| needle grama | BOAR | Bouteloua aristidoides | 0–5 | – | ||
| sixweeks grama | BOBA2 | Bouteloua barbata | 0–5 | – | ||
| Rothrock's grama | BORO2 | Bouteloua rothrockii | 0–3 | – | ||
| Arizona brome | BRAR4 | Bromus arizonicus | 0–1 | – | ||
| tufted lovegrass | ERPEP2 | Eragrostis pectinacea var. pectinacea | 0–1 | – | ||
| Mexican sprangletop | LEFUU | Leptochloa fusca ssp. uninervia | 0–1 | – | ||
| mucronate sprangletop | LEPA6 | Leptochloa panicea | 0–1 | – | ||
| delicate muhly | MUFR | Muhlenbergia fragilis | 0–1 | – | ||
| littleseed muhly | MUMI | Muhlenbergia microsperma | 0–1 | – | ||
| witchgrass | PACA6 | Panicum capillare | 0–1 | – | ||
| Hall's panicgrass | PAHA | Panicum hallii | 0–1 | – | ||
| Bigelow's bluegrass | POBI | Poa bigelovii | 0–1 | – | ||
| Eastwood fescue | VUMIC | Vulpia microstachys var. ciliata | 0–1 | – | ||
| Pacific fescue | VUMIP | Vulpia microstachys var. pauciflora | 0–1 | – | ||
|
Forb
|
||||||
| 3 | 10–25 | |||||
| tree tobacco | NIGL | Nicotiana glauca | 1000–5000 | – | ||
| slender janusia | JAGR | Janusia gracilis | 2–5 | – | ||
| narrowleaf silverbush | ARLA12 | Argythamnia lanceolata | 0–3 | – | ||
| New Mexico silverbush | ARNE2 | Argythamnia neomexicana | 0–3 | – | ||
| slender poreleaf | POGR5 | Porophyllum gracile | 0–3 | – | ||
| desert globemallow | SPAM2 | Sphaeralcea ambigua | 0–3 | – | ||
| brownplume wirelettuce | STPA4 | Stephanomeria pauciflora | 0–1 | – | ||
| Parry's beardtongue | PEPA24 | Penstemon parryi | 0–1 | – | ||
| bluedicks | DICAC5 | Dichelostemma capitatum ssp. capitatum | 0–1 | – | ||
| desert trumpet | ERIN4 | Eriogonum inflatum | 0–1 | – | ||
| moleplant | EULA4 | Euphorbia lathyris | 0–1 | – | ||
| California fagonbush | FALA | Fagonia laevis | 0–1 | – | ||
| desert rosemallow | HICO | Hibiscus coulteri | 0–1 | – | ||
| Newberry's velvetmallow | HONE | Horsfordia newberryi | 0–1 | – | ||
| lacy tansyaster | MAPI | Machaeranthera pinnatifida | 0–1 | – | ||
| rough menodora | MESC | Menodora scabra | 0–1 | – | ||
| San Felipe dogweed | ADPO | Adenophyllum porophylloides | 0–1 | – | ||
| trailing windmills | ALIN | Allionia incarnata | 0–1 | – | ||
| 4 | 5–50 | |||||
| desert Indianwheat | PLOV | Plantago ovata | 0–10 | – | ||
| woolly plantain | PLPA2 | Plantago patagonica | 0–10 | – | ||
| common fiddleneck | AMMEI2 | Amsinckia menziesii var. intermedia | 0–5 | – | ||
| western tansymustard | DEPI | Descurainia pinnata | 0–3 | – | ||
| combseed | PECTO | Pectocarya | 0–3 | – | ||
| Emory's rockdaisy | PEEM | Perityle emoryi | 0–1 | – | ||
| cliffbrake | PELLA | Pellaea | 0–1 | – | ||
| phacelia | PHACE | Phacelia | 0–1 | – | ||
| Mojave woodyaster | XYTOT | Xylorhiza tortifolia var. tortifolia | 0–1 | – | ||
| New Mexico plumeseed | RANE | Rafinesquia neomexicana | 0–1 | – | ||
| chia | SACO6 | Salvia columbariae | 0–1 | – | ||
| ragwort | SENEC | Senecio | 0–1 | – | ||
| sleepy silene | SIAN2 | Silene antirrhina | 0–1 | – | ||
| Coulter's globemallow | SPCO2 | Sphaeralcea coulteri | 0–1 | – | ||
| woollyhead neststraw | STMI2 | Stylocline micropoides | 0–1 | – | ||
| woolly tidestromia | TILA2 | Tidestromia lanuginosa | 0–1 | – | ||
| tall mountain larkspur | DESC | Delphinium scaposum | 0–1 | – | ||
| wedgeleaf draba | DRCU | Draba cuneifolia | 0–1 | – | ||
| whisperingbells | EMPE | Emmenanthe penduliflora | 0–1 | – | ||
| flatcrown buckwheat | ERDE6 | Eriogonum deflexum | 0–1 | – | ||
| miniature woollystar | ERDI2 | Eriastrum diffusum | 0–1 | – | ||
| fleabane | ERIGE2 | Erigeron | 0–1 | – | ||
| buckwheat | ERIOG | Eriogonum | 0–1 | – | ||
| Texas stork's bill | ERTE13 | Erodium texanum | 0–1 | – | ||
| California poppy | ESCAM | Eschscholzia californica ssp. mexicana | 0–1 | – | ||
| desert poppy | ESGL | Eschscholzia glyptosperma | 0–1 | – | ||
| spotted hideseed | EUCH | Eucrypta chrysanthemifolia | 0–1 | – | ||
| gilia | GILIA | Gilia | 0–1 | – | ||
| Gordon's bladderpod | LEGO | Lesquerella gordonii | 0–1 | – | ||
| pepperweed | LEPID | Lepidium | 0–1 | – | ||
| Bigelow's linanthus | LIBI2 | Linanthus bigelovii | 0–1 | – | ||
| foothill deervetch | LOHU2 | Lotus humistratus | 0–1 | – | ||
| desert deervetch | LOMI | Lotus micranthus | 0–1 | – | ||
| coastal bird's-foot trefoil | LOSA | Lotus salsuginosus | 0–1 | – | ||
| Coulter's lupine | LUSP2 | Lupinus sparsiflorus | 0–1 | – | ||
| Parry's false prairie-clover | MAPA7 | Marina parryi | 0–1 | – | ||
| blazingstar | MENTZ | Mentzelia | 0–1 | – | ||
| Nuttall's povertyweed | MONU | Monolepis nuttalliana | 0–1 | – | ||
| green carpetweed | MOVE | Mollugo verticillata | 0–1 | – | ||
| cloak fern | NOTHO | Notholaena | 0–1 | – | ||
| evening primrose | OENOT | Oenothera | 0–1 | – | ||
| Florida pellitory | PAFL3 | Parietaria floridana | 0–1 | – | ||
| carelessweed | AMPA | Amaranthus palmeri | 0–1 | – | ||
| rockcress | ARABI2 | Arabis | 0–1 | – | ||
| milkvetch | ASTRA | Astragalus | 0–1 | – | ||
| Coulter's spiderling | BOCO2 | Boerhavia coulteri | 0–1 | – | ||
| spiderling | BOERH2 | Boerhavia | 0–1 | – | ||
| hoary bowlesia | BOIN3 | Bowlesia incana | 0–1 | – | ||
| California suncup | CACA32 | Camissonia californica | 0–1 | – | ||
| exserted Indian paintbrush | CAEXE | Castilleja exserta ssp. exserta | 0–1 | – | ||
| mariposa lily | CALOC | Calochortus | 0–1 | – | ||
| white tackstem | CAWR | Calycoseris wrightii | 0–1 | – | ||
| pebble pincushion | CHCA | Chaenactis carphoclinia | 0–1 | – | ||
| lipfern | CHEIL | Cheilanthes | 0–1 | – | ||
| devil's spineflower | CHRI | Chorizanthe rigida | 0–1 | – | ||
| Esteve's pincushion | CHST | Chaenactis stevioides | 0–1 | – | ||
| New Mexico thistle | CINE | Cirsium neomexicanum | 0–1 | – | ||
| cryptantha | CRYPT | Cryptantha | 0–1 | – | ||
| hairy prairie clover | DAMO | Dalea mollis | 0–1 | – | ||
| American wild carrot | DAPU3 | Daucus pusillus | 0–1 | – | ||
| desert larkspur | DEPA | Delphinium parishii | 0–1 | – | ||
|
Shrub/Vine
|
||||||
| 5 | 100–175 | |||||
| triangle bur ragweed | AMDE4 | Ambrosia deltoidea | 100–175 | – | ||
| 6 | 150–200 | |||||
| yellow paloverde | PAMI5 | Parkinsonia microphylla | 120–175 | – | ||
| water jacket | LYAN | Lycium andersonii | 2–10 | – | ||
| Fremont's desert-thorn | LYFR | Lycium fremontii | 2–10 | – | ||
| creosote bush | LATRT | Larrea tridentata var. tridentata | 2–5 | – | ||
| 7 | 25–50 | |||||
| 8 | 5–50 | |||||
| velvet mesquite | PRVE | Prosopis velutina | 4–43 | – | ||
| arrow poision plant | SEBI9 | Sebastiania bilocularis | 0–5 | – | ||
| desert lavender | HYEM | Hyptis emoryi | 0–3 | – | ||
| sangre de cristo | JACA2 | Jatropha cardiophylla | 0–3 | – | ||
| Sonoran croton | CRSO | Croton sonorae | 0–3 | – | ||
| pelotazo | ABIN | Abutilon incanum | 0–2 | – | ||
| California copperleaf | ACCA3 | Acalypha californica | 0–2 | – | ||
| Wright's beebrush | ALWR | Aloysia wrightii | 0–1 | – | ||
| horsetail milkweed | ASSU2 | Asclepias subverticillata | 0–1 | – | ||
| brittlebush | ENFA | Encelia farinosa | 0–1 | – | ||
| Nevada jointfir | EPNE | Ephedra nevadensis | 0–1 | – | ||
| bastardsage | ERWR | Eriogonum wrightii | 0–1 | – | ||
| starry bedstraw | GASTE2 | Galium stellatum ssp. eremicum | 0–1 | – | ||
| sweetbush | BEJU | Bebbia juncea | 0–1 | – | ||
| spearleaf brickellbush | BRAT | Brickellia atractyloides | 0–1 | – | ||
| Coulter's brickellbush | BRCO | Brickellia coulteri | 0–1 | – | ||
| fragrant bursera | BUFA | Bursera fagaroides | 0–1 | – | ||
| elephant tree | BUMI | Bursera microphylla | 0–1 | – | ||
| ragged rockflower | CRBI2 | Crossosoma bigelovii | 0–1 | – | ||
| littleleaf ratany | KRER | Krameria erecta | 0–1 | – | ||
| white ratany | KRGR | Krameria grayi | 0–1 | – | ||
| desert ironwood | OLTE | Olneya tesota | 0–1 | – | ||
| jojoba | SICH | Simmondsia chinensis | 0–1 | – | ||
| American threefold | TRCA8 | Trixis californica | 0–1 | – | ||
| 9 | Succulents | 5–50 | ||||
| ocotillo | FOSP2 | Fouquieria splendens | 5–10 | – | ||
| organpipe cactus | STTH3 | Stenocereus thurberi | 0–3 | – | ||
| senita cactus | PASC14 | Pachycereus schottii | 0–2 | – | ||
| beavertail pricklypear | OPBA2 | Opuntia basilaris | 0–2 | – | ||
| Emory's barrel cactus | FEEM | Ferocactus emoryi | 0–2 | – | ||
| candy barrelcactus | FEWI | Ferocactus wislizeni | 0–2 | – | ||
| Thornber's nipple cactus | MATH | Mammillaria thornberi | 0–1 | – | ||
| Engelmann's hedgehog cactus | ECEN | Echinocereus engelmannii | 0–1 | – | ||
Interpretations
Animal community
Steep slopes, cobbly and gravelly surfaces and large areas of rock outcrop severely limit livestock distribution. Stocker cattle are best adapted to use areas of this site. The plant community provides limited amounts of usable forage in the winter-spring season. Normal water is lacking.
Water developments are very important to wildlife species on this site. Cover, diversity and topography make this site home to a variety of desert animals. Large mammals use the sute seasonally unless permanent water supplies exist nearby. The high percentage of bluff and rim outcrops make this site a favorite one for bighorn sheep. Javalina bed in numerous caves and rock shelters which occur on this site. Desert tortoises use the smaller caverns on southern exposures for winter dens. Caves and shelters in bluffs are also important for several bat species and for honey bees.
Other information
T&E Species: lesser long-nosed bat
Supporting information
Contributors
Dan Robinett
Dan Robinett, J. Norris
Larry D. Ellicott
Steve Barker
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) | Dave Womack, Dan Robinett, Emilio Carrillo |
|---|---|
| Contact for lead author | NRCS Tucson Area Office |
| Date | 12/28/2005 |
| Approved by | S. Cassady |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
Common on the site only in areas where rock and gravel cover is low. Rills follow joints, fractures and bedding planes in the bedrock parent materials. -
Presence of water flow patterns:
Water flow patterns are common, continuous and cover 15-20% of area. -
Number and height of erosional pedestals or terracettes:
No pedestals or terracettes on the site. -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
1-5% -
Number of gullies and erosion associated with gullies:
none -
Extent of wind scoured, blowouts and/or depositional areas:
No evidence of soil movement by wind. -
Amount of litter movement (describe size and distance expected to travel):
Herbaceous litter can move by wind and water. Woody litter remains under shrub canopies. -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Soil surface resistance to erosion is good uncer shrub canopipes & areas with high rock and gravel cover to moderate in soil interspaces due to crusts formed by raindrop impact. -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Weak thin platy to granular, to 3 inches thick. -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Canopy 10-20%; 90-95% trees, 2-5% shrubs, 1-2% half shrubs, 1-2% succulents. Cover is well dispersed throughout the site. -
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:
trees > large shrubs = half shrubs > winter annuals > summer annuals > perennial grasses and forbs > cryptogams (Note: In El Nino years, annual forbs and grasses are #1 in above ground weight.)Sub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
0-50% canopy mortality -
Average percent litter cover (%) and depth ( in):
Herbaceous litter is not persistent on the site and may be 20-60% in El Nino years. -
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
300 lbs/ac unfavorable precipitation; 500 lbs/ac normal precipitation; 750 lbs/ac favorable precipitation. -
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:
Sahara mustard (potential) -
Perennial plant reproductive capability:
Not impaired for shrubs, drought impaired for perennial grasses and forbs.
Print Options
Sections
Font
Other
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.
Click on box and path labels to scroll to the respective text.