Southern Idaho (ID footprint); partial normalized coverage · 2013-11-08
The official database labels itself "For Southern Idaho" and describes Idaho residents at the urban-rangeland interface. FireApproved publishes 419 existing plant owners that cite its scored rows. This bounded Southern Idaho scope is regional context, not statewide coverage or a conclusion that the score transfers unchanged to every Idaho site.
Arizona at or above 3,000 feet (AZ footprint); partial normalized coverage · 2011-12-01
AZ1289 is explicitly limited to Arizona elevations of 3,000 feet and higher. FireApproved publishes 69 exact owners as regional Arizona context, retaining every water and elevation condition. It is never promoted to statewide low-desert guidance or an independent Tier 1 vote.
Yavapai County (AZ footprint); partial normalized coverage · 2025-03-14
University of Arizona Cooperative Extension authors Bulletin 34 for Yavapai County. FireApproved publishes 198 exact source owners from its resistant and prone tables and keeps the county boundary visible. County publication scope is regional Arizona context, never statewide scope.
2. Why this plant is relevant here
State distribution
Documented in AZ, CA, CO, DC, ID, IL, KS, KY, MO, MT, ND, NE, NM, NV, OK, OR, SD, TX, UT, WA, WY.
Native range
Current cited native range in AZ, CA, CO, ID, KS, MT, ND, NE, NM, NV, OK, OR, SD, TX, UT, WA, WY.
Introduced / established
1 sourced range or established record; set a location to match them. This is not an invasive warning.
USDA hardiness
Documented minimum 2b; no upper limit is documented.
3. Legal, ecological, and broader status
Legal-list status
Set a location for an exact legal-list result; source silence is not clearance.
Seed-list status
Set a location to compare the separate state noxious-weed seed layer.
Reported invasive here
No ecological invasive report is normalized; that does not prove noninvasiveness.
Broader regional context
Aggregate AK, HI, and L48 evidence is shown only as regional context, never as an exact-state finding.
Federal context
Federal designations remain separate from state legal-list results.
How to read this page
The status above is computed from the cited rows below: independent recommendations can support a fire-resistant result, an avoid row can produce keep-away, and disagreement stays visible as conflict. Placement notes preserve each source’s own scheme rather than translating unlike rules into one scale. This is evidence about a plant, not permission to plant it in every part of the defensible space; Zone 0 remains noncombustible.
Photo: no rights reserved (CC0),
via iNaturalist. Species-typical, not necessarily this cultivar.
Form
grass
USDA hardiness
Minimum 2b; upper limit not documented
Mature height
~1.5 ft
Water need
low
Current cited native range
AZ, CA, CO, ID, KS, MT, ND, NE, NM, NV, OK, OR, SD, TX, UT, WA, WY
Grows in
AZ, CA, CO, DC, ID, IL, KS, KY +13
Rated in
Arizona above 3,000 feet / interior Southwest; British Columbia; Global; Great Basin +3
Family
Poaceae
Evidence
10 cited sources
Native and introduced range evidence
These are exact U.S. botanical-area records from the cited range source. Native and
introduced describe biogeographic relationship, not fire performance or planting approval.
Doubtful and extinct rows stay visible but do not count as current presence.
The lossless worldwide derivative is retained once in the research corpus; object pages repeat only exact U.S. areas needed by the local lens. The JSON twin carries the same page assertions.
Plant hardiness evidence
These values describe the plant source. Your ZIP zone comes from the separate 2023 USDA
Plant Hardiness Zone Map. Whole-zone values stay whole-zone, and a single unresolved value
is not treated as a tolerance range. Different source boundaries stay separate: overlapping
statements are compared independently, while only ranges with no shared zone are called a conflict.
Source location: PlantCharacteristics record 22420, Temperature, Minimum (°F).
Where its sources say to plant it
Placement rules below use each source's own distances or named zones, tied to its rating.
They are not interchangeable with the directory's current Zone 0 guidance.
Fire Resistance of Plants Master Database: plantable at 80' from home [Idaho minimum planting distance] (with its avoid rating)
FireSmart BC Plant Program: suitable for HIZ extended zone and beyond [FireSmart BC Home Ignition Zone] (with its recommendation)
Fuel Breaks to Reduce Large Wildfire Impacts in Sagebrush…: common plant material option for a managed greenstrip in sagebrush ecosystems [nrcs-tn66-greenstrip] (with its recommendation)
Forage Kochia Helps Fight Range Fires: species used in a semiarid western rangeland greenstrip [harrison-2002-greenstrip] (with its recommendation)
The evidence
Grouped by what each source concluded. Primary evidence rated the plant itself
(a lab, field program, or original curation); corroboration compiled or
republished another source's rating and resolves to its root lineage.
Appendix B row: Bottlebrush Squirreltail (Elymus elymoides). Origin: Native; lifeform: Bunchgrass; relative height: Low; seedling vigor: Med.; longevity: Long. Precipitation zone: 8-18 in; soil texture: medium and coarse; seeds/lb: 220,000; single-species drill seeding rate: 7 lb/ac; seeding depth: 1/4-1/2 in. Recommended releases: Fish Creek, Toe Jam Creek, Rattlesnake, Pueblo, Wapiti, Pleasant Valley, Antelope Creek.
Table 1 row: bottlebrush squirreltail — Elymus elymoides (Raf.) Swezey. The article says these are species frequently used in greenstrips; it does not report a separate burn result for this row.
Listed as Squirreltail grass — Elymus elymoides. The bulletin says fire-resistant plants tend to resist ignition when irrigated and maintained, while fire-prone plants may ignite readily and burn intensely.
4 cited rows from this source; its identity, lineage and tier are stated once.
“time to flaming (s): 2.598”
· score 2.598 (FLAMITS — time to flaming (s))
FLAMITS record 17354; Ignitability measurement; plant part whole plant; fuel live; predrying yes; device burning bench; site Gao2018-1; sampling june to august 2016. Primary study Gao2018: Gao, X., & Schwilk, D. W. (2018). Grass Canopy Architecture Influences Temperature Exposure at Soil Surface. Fire 1, 35.
FLAMITS record 17355; Sustainability measurement; plant part whole plant; fuel live; predrying yes; device burning bench; site Gao2018-1; sampling june to august 2016. Primary study Gao2018: Gao, X., & Schwilk, D. W. (2018). Grass Canopy Architecture Influences Temperature Exposure at Soil Surface. Fire 1, 35.
FLAMITS record 17356; Sustainability measurement; plant part whole plant; fuel live; predrying yes; device burning bench; site Gao2018-1; sampling june to august 2016. Primary study Gao2018: Gao, X., & Schwilk, D. W. (2018). Grass Canopy Architecture Influences Temperature Exposure at Soil Surface. Fire 1, 35.
FLAMITS record 17357; Combustibility measurement; plant part whole plant; fuel live; predrying yes; device burning bench; site Gao2018-1; sampling june to august 2016. Primary study Gao2018: Gao, X., & Schwilk, D. W. (2018). Grass Canopy Architecture Influences Temperature Exposure at Soil Surface. Fire 1, 35.