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Ecological site R039XA137AZ

Loamy Upland 17-22" p.z. Subirrigated

Last updated: 4/06/2020
Accessed: 11/21/2024

Home / Esd catalog / MLRA 039X / Ecological site R039XA137AZ

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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.

MLRA notes

Major Land Resource Area (MLRA): 039X–Mogollon Transition North

AZ 39.1 Mogollon Plateau Coniferous Forests

Elevations range from 7000 to 12,500 feet and precipitation averages 20 to 35 inches per year. Vegetation includes ponderosa pine, Gambel oak, Arizona walnut, sycamore, Douglas fir, blue spruce, Arizona fescue, sheep fescue, mountain muhly, muttongrass, junegrass, pine dropseed, and dryland sedges. The soil temperature regime ranges from mesic to frigid and the soil moisture regime ranges from typic ustic to udic ustic. This unit occurs within the Colorado Plateau Physiographic Province and is characterized by a sequence of flat to gently dipping sedimentary rocks eroded into plateaus, valleys and deep canyons. Sedimentary rock classes dominate the plateau with volcanic fields occurring for the most part near its margin.

Associated sites

R039XA130AZ	Loamy Bottom 17-22" p.z.
R039XA138AZ	Clay Loam Upland 17-22 p.z.

R039XA130AZ

Loamy Bottom 17-22" p.z.

R039XA138AZ

Clay Loam Upland 17-22 p.z.

Table 1. Dominant plant species

Tree	(1) Pinus ponderosa
Shrub	(1) Ericameria nauseosa ssp. nauseosa var. glabrata
Herbaceous	(1) Juncus (2) Carex

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Physiographic features

This site occurs on the backslopes and breaks of basalt plateaus. The soils are deep and are saturated except in the driest conditions. The site does benefit significantly from ground water transmission, but benefits not at all or only slightly from run-on moisture from adjacent areas.

Table 2. Representative physiographic features

Landforms	(1) Plateau
Elevation	6,000 – 8,000 ft
Slope	1 – 10%
Aspect	Aspect is not a significant factor

Climatic features

About 40% of the moisture in this Common Resource Area (CRA), or Land Resource Unit (LRU) comes as rain from June to September. The remainder comes from October to May as snow or light rain. Extreme temperatures of 97 and -37 degrees Fahrenheit have been recorded. Some moisture is usually received every month.

Table 3. Representative climatic features

Frost-free period (average)	168 days
Freeze-free period (average)	120 days
Precipitation total (average)	22 in

Bar

Line

Figure 1. Monthly precipitation range

Bar

Line

Figure 2. Monthly average minimum and maximum temperature

Soil features

The soils characterizing this site are deep to basalt bedrock. They are saturated by groundwater tranmission except in the driest of conditions. The surface soil textures include cobbly loam and is generally covered by about 3 inches of highly decomposed plant material. The subsurface textures include very cobbly and extremely cobbly clay loam.
Typical taxonomic units include: SSA 695 Navajo Depot - MU 12 Oxley family cobbly loam.

Table 4. Representative soil features

Surface texture	(1) Cobbly loam
Family particle size	(1) Loamy
Drainage class	Somewhat poorly drained to poorly drained
Permeability class	Moderately slow to slow
Soil depth	40 – 60 in
Surface fragment cover <=3"	10 – 15%
Subsurface fragment volume <=3" (Depth not specified)	20 – 55%

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 grazing, fire, 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 shown for the group. Divide the resulting total by the total normal year production shown in the plant community description. If 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
Click on state and transition labels to scroll to the respective text

Ecosystem states

1. Grass Dominant: spike muhly, canada bluegrass, scattered ponderosa pine, and scattered rubber rabbitbrush

2. Shrub Dominant: rubber rabbitbrush

State 1 submodel, plant communities

1.1. Historic Climax Plant Community

State 1
Grass Dominant: spike muhly, canada bluegrass, scattered ponderosa pine, and scattered rubber rabbitbrush

This state is grass dominant with scattered trees and shrubs.

Community 1.1
Historic Climax Plant Community

The historic climax plant community of this site is dominated by a variety of grasses and forbs.

Figure 3. Annual production by plant type (representative values) or group (midpoint values)

Table 5. Annual production by plant type

Plant type	Low (lb/acre)	Representative value (lb/acre)	High (lb/acre)
Grass/Grasslike	720	740	760
Forb	40	60	80
Shrub/Vine	0	8	16
Tree	0	4	8
Total	760	812	864

Figure 4. Plant community growth curve (percent production by month). AZ3911, 39.1 17-22" p.z. all sites. Growth begins in the spring, most growth occurs during the summer rainy season..

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	10	10	10	20	20	20	5	0	0

State 2
Shrub Dominant: rubber rabbitbrush

This state shows a decrease in grass and an increase in rubber rabbitbrush.

Transition T1A
State 1 to 2

Excessive disturbance such as periodic fire, ground disturbing recreation, and continuous, season-long grazing will cause a threshold to be crossed to a rubber rabbitbrush state.

Restoration pathway R2A
State 2 to 1

An increase in soil organic carbon and a decrease in bare ground will help restore the system.

Additional community tables

Table 6. Community 1.1 plant community composition

Group	Common name	Symbol	Scientific name	Annual production (lb/acre)	Foliar cover (%)
Tree
1				0–6
	ponderosa pine	PIPO	Pinus ponderosa	0–6	–
Shrub/Vine
2				0–30
	rubber rabbitbrush	ERNAG	Ericameria nauseosa ssp. nauseosa var. glabrata	0–13	–
	pingue rubberweed	HYRI	Hymenoxys richardsonii	0–13	–
	Woods' rose	ROWOW	Rosa woodsii var. woodsii	0–6	–
3				6–25
	aster	ASTER	Aster	6–13	–
	cinquefoil	POTEN	Potentilla	0–6	–
	sandwort	ARENA	Arenaria	0–6	–
Grass/Grasslike
3				150–375
	spike muhly	MUWR	Muhlenbergia wrightii	98–195	–
	deergrass	MURI2	Muhlenbergia rigens	32–65	–
	mountain muhly	MUMO	Muhlenbergia montana	0–32	–
	pine dropseed	BLTR	Blepharoneuron tricholepis	0–32	–
	Ross' sedge	CARO5	Carex rossii	6–20	–
	rush	JUNCU	Juncus	6–20	–
	Grass, annual	2GA	Grass, annual	6–13	–
	little bluestem	SCSC	Schizachyrium scoparium	0–6	–
	nodding brome	BRAN	Bromus anomalus	0–6	–
1				115–240
	Canada bluegrass	POCO	Poa compressa	98–162	–
	slender wheatgrass	ELTRT	Elymus trachycaulus ssp. trachycaulus	6–20	–
	western wheatgrass	PASM	Pascopyrum smithii	6–20	–
	squirreltail	ELELE	Elymus elymoides ssp. elymoides	6–13	–
	Arizona fescue	FEAR2	Festuca arizonica	0–6	–
	prairie Junegrass	KOMA	Koeleria macrantha	0–6	–
	Fendler's threeawn	ARPUF	Aristida purpurea var. fendleriana	0–6	–
	muttongrass	POFE	Poa fendleriana	0–6	–
2				10–65
	mat muhly	MURI	Muhlenbergia richardsonis	0–32	–
	blue grama	BOGR2	Bouteloua gracilis	8–20	–
	tufted hairgrass	DECE	Deschampsia cespitosa	0–13	–
Forb
4				25–105
	iris	IRIS	Iris	6–13	–
	Lewis flax	LILE3	Linum lewisii	6–13	–
	western yarrow	ACMIO	Achillea millefolium var. occidentalis	6–13	–
	pussytoes	ANTEN	Antennaria	6–13	–
	white sagebrush	ARLU	Artemisia ludoviciana	0–6	–
	milkvetch	ASTRA	Astragalus	0–6	–
	thistle	CIRSI	Cirsium	0–6	–
	horsetail	EQUIS	Equisetum	0–6	–
	redroot buckwheat	ERRA3	Eriogonum racemosum	0–6	–
	strawberry	FRAGA	Fragaria	0–6	–
	lupine	LUPIN	Lupinus	0–6	–
	dock	RUMEX	Rumex	0–6	–

Supporting information

Type locality

Location 1: Coconino County, AZ
Township/Range/Section	T21N R5E S10
General legal description	Belmont, AZ quad, NE1/4, NE1/4, Section 10, T21N, R5E, Camp Navajo, Coconino County, AZ.

Contributors

Larry D. Ellicott
Steve Barker

Approval

Scott Woodall, 4/06/2020

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	09/10/2022
Approved by	Scott Woodall
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:

Download reference sheet