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Compact Brome

Bromus madritensis L.

Associations

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Foodplant / parasite
Blumeria graminis parasitises live Anisantha madritensis

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Description

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Annual. Culms loosely tufted, simple, erect or geniculately ascending, 40–60 cm tall, glabrous. Leaf sheaths hairy, at least the lower; leaf blades linear-lanceolate, flat, ca. 20 cm × 2–4 mm, glabrous or pubescent, margins scabrid, apex acuminate; ligule 1.5–4 mm. Panicle dense or slightly lax, erect, 4–15 × 2–6 cm; branches 2–3 per node, 1–3 cm, hairy, sometimes branched. Spikelets oblong, flabellate at maturity, 35–60 mm, florets 6–13, lax; lower glume subulate, 6–11 mm, 1-veined, upper glume linear-lanceolate, 10–16 mm, 3-veined; lemmas oblong, 12–19 × 3–3.5 mm in side view, 7-veined, glabrous or pubescent, margins inrolled, apex acuminate, 2-toothed; awn 12–18 mm, straight or weakly recurved; palea shorter than lemma. Stamens 2, anthers ca. 1 mm. Fl. May–Aug. 2n = 14, 28.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 22: 373, 381 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
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Flora of China @ eFloras.org
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Wu Zhengyi, Peter H. Raven & Hong Deyuan
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Distribution

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Xizang [N Africa, America, SW Asia (Iran, Iraq), Europe].
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 22: 373, 381 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
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eFloras.org
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Habitat

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Sunny slopes, dry sandy grassy places; ca. 3500 m.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 22: 373, 381 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
project
eFloras.org
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eFloras

Synonym

provided by eFloras
Anisantha madritensis (Linnaeus) Nevski; Festuca madri-tensis (Linnaeus) Desfontaines; Genea madritensis (Linnaeus) Dumortier; Zerna madritensis (Linnaeus) Panzer ex B. D. Jackson.
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cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 22: 373, 381 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
project
eFloras.org
original
visit source
partner site
eFloras

Broad-scale Impacts of Plant Response to Fire

provided by Fire Effects Information System Plants
More info for the terms: association, controlled burn, cover, density, fire frequency, frequency, grassland, prescribed fire, presence, shrub, wildfire

Red brome showed dramatic increases in the Sonoran Desert following prescribed burns
in a desert scrub of paloverde, buckhorn cholla (Opuntia acanthocarpa), and
triangle bursage.
Results are summarized below [58]:



Cover (%) within open microhabitat:


Control 1985
Control 1986
Prefire 1985
12 postfire months (1985)
24 postfire months (1985)*
36 postfire months (1986)*

1.02
0.48
3.56
7.22
11.81
12.89




Cover (%) in shrub microhabitat:


Control 1985
Control 1986
Prefire 1985
12 postfire months (1985)
24 postfire months (1985)*
36 postfire months (1986)*

0.68
4.77
7.42
9.17
11.67
26.61


*Coverage data taken from areas burned in 1983




Davis and Hickson [29] evaluated postfire vegetation
development within coastal chaparral of California. Past fires in the area studied was
either accidental or
planned burns. Areas sampled ranged from 1 to 50 years since fire. Overall, red
brome showed greater frequency of occurrence within oak plots than in
shrub plots.
Red brome was an important invader of chamise chaparral in the 3rd and 5th postfire seasons,
slowly disappearing with increased brush cover. Before fires, red brome was restricted to
trails, firebreaks, and openings [42].


Red brome was a dominant species on western and southern slopes (330 feet (100 m)) the first

2 years after fire in California coastal sage scrub. Postfire annual precipitation was 1 to 5 times
greater than mean annual precipitation [51].



Fall burns: Red brome and California buckwheat were dominant species 5 years
after a September wildfire in a 7-year-old rockrose (Cistus spp.) field, originally
planted from nursery grown seedlings. The wildfire occurred on a 30 to 35 degree north facing slope at
2,700 feet (820 m). [61].



Hansen [39] observed postfire coverage of red brome after fall prescribed burns in the Tulare
Basin of California.
Seasonal precipitation directly influenced red brome postfire response. One-year postfire
cover of red brome was equal to or greater than control plot coverage when precipitation was below average and
the majority of precipitation occurred in the fall (September-November). In contrast, red brome
presence was greatly reduced in the 1st and 2nd postfire growing season if greater than
normal precipitation occurred in fall and spring. Repeated burning had the greatest negative
effect on red brome numbers, resulting in large decreases even in wet years.



Spring burns: Cave [26] monitored 1- and 2-year postfire vegetation response in the
Sonoran Desert after a 12 June 1981 controlled burn and a 26 April 1980
wildfire. Sites were at 1,500 feet (450 m) on a paloverde (Cercidium microphyllum)-cactus (Opuntia
spp.)-triangle bursage association. Red brome density was reduced by 96 to 98%
in the
1st postfire year compared to unburned and prefire controlled burn sites, respectively. Biomass
was reduced by 70 and 65%, with cover showing 86 and 80% reductions.
Precipitation prior to and during the 1982 growing season was less than
precipitation in 1981.



Red brome dominated blackbrush areas 1 year after a "hot" spring wildfire [9].



For information on response of red brome and other annual grassland herbs
to prescribed fire, see Hansen's [39] thesis: The effect of fire and fire
frequency on grassland species composition in California's Tulare Basin.pdf
.
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bibliographic citation
Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Common Names

provided by Fire Effects Information System Plants
foxtail chess

compact brome

Spanish brome



red brome
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bibliographic citation
Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Cover Value

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More info for the term: cover

Foxtail chess provides fair cover for small mammals and small nongame birds [30].
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Description

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More info for the term: cool-season

Foxtail chess and reed brome are a cool-season [64] exotic annual grasses with culms from 4 to 28 inches (10-70 cm) tall. Their inflorescence is a panicle, 1 to 4 inches (3-11 cm) tall, with long awns [66]. Foxtail chess is distinguished from red brome by having relatively hairier stems and leaf sheaths, more lax panicles, and wider lemmas [1,41].

Foxtail chess is drought resistant, with high water-use efficiency [10,21].
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bibliographic citation
Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Distribution

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Foxtail chess is native throughout Europe and the British Isles [36,41,46,49,76,80,83]. In western North America, it occurs widely in coastal and central California and is also recorded from Reno, Nevada, and Portland, Oregon [66,84]. It has a scattered distribution to the east, occurring in Michigan, Virginia, and Mississippi [47]. It is also introduced in Hawaii [75].

Red brome is native to southern Europe [80]. In North America, it is distributed from central Washington south to Baja California and east to central Idaho, southwestern Texas, and Sonora [66,84]. It is casually adventive in the Northeast [36] and introduced in Hawaii [75]. PLANTS database provides distributional maps of foxtail chess and of red brome.

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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Fire Ecology

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More info for the terms: cover, fire frequency, fire regime, forbs, frequency, herb, litter, nonnative species, presence, seed, shrub, shrubs, woodland

Red brome generally shortens fire return intervals [59,60,87]. The increased presence of red brome has promoted fires in areas where fire was previously infrequent due to insufficient fuels [68]. Once established red brome may increase fire frequency by enhancing potential for start and spread [10]. In general, red brome produces an abundant and continuous cover of persistent fine fuels, promoting fast, "hot" fires [21].

Desert: Areas of the Mojave Desert dominated by red brome are more susceptible to fire than areas dominated by native forbs. Dead red brome culms and blades are persistent (commonly 2 years); herbage of most Mojave Desert annual species usually lasts 1 year or less. Red brome produces high amounts of persistent flammable fuels in perennial plant interspaces, promoting ignition and spread [22].

Heat generated by burning red brome is sufficient to ignite and consume dead stems of native Mojave Desert forbs. Flames may also consume small shrubs such as white bursage (Ambrosia dumosa), winterfat (Krascheninnikovia lanata), white burrobush, and Anderson wolfberry (Lycium andersonii). However, flames fueled by red brome are generally insufficient to ignite large shrubs such as creosote bush [21].

Within the Sonoran Desert, dead and dry red brome is easily ignited, supporting fast-moving surface fires [68]. Fire return intervals are also shortened, changing the vegetal composition through increase of non-native components and loss of native plant species [72].

California chaparral:  The invasion of red brome has contributed to short fire return intervals and the subsequent degradation of chaparral [87]. Keeley [50] has observed shorter fire intervals (< 10 years) resulting from the increased presence of red brome and other exotic annuals. Greater fire frequency has promoted the degradation of native herb communities and promoted communities of chaparral shrubs with an exotic, annual understory [87]. Dead stems and litter are persistent, promoting spread of fire in shrub communities, especially across areas between shrubs and trees [44,87].

O'Leary and Westman [63] attribute red brome within early postfire coastal sage scrub communities to off-site seed sources.

FIRE REGIMES:
As nonnative species, foxtail chess and red brome have no historic fire regime in North America. The following table provides some fire regime intervals for areas where foxtail chess and red brome presently occur. Foxtail chess and red brome may alter fire intervals within these communities. Find further fire regime information for the plant communities in which these species may occur by entering the species' names in the FEIS home page under "Find FIRE REGIMES".

California chaparral Adenostoma and/or Arctostaphylos spp. sagebrush steppe Artemisia tridentata/Pseudoroegneria spicata 20-70 coastal sagebrush Artemisia californica cheatgrass Bromus tectorum California montane chaparral Ceanothus and/or Arctostaphylos spp. 50-100 paloverde-cactus shrub Cercidium microphyllum/Opuntia spp. mountain-mahogany-Gambel oak scrub Cercocarpus ledifolius-Quercus gambelii blackbrush Coleogyne ramosissima creosotebush Larrea tridentata Ceniza shrub Larrea tridentata-Leucophyllum frutescens-Prosopis glandulosa California oakwoods Quercus spp. oak-juniper woodland (Southwest) Quercus-Juniperus spp. blue oak-foothills pine Quercus douglasii-Pinus sabiana bur oak Quercus macrocarpa interior live oak Quercus wislizenii 24]
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Growth Form (according to Raunkiær Life-form classification)

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More info on this topic.

More info for the term: therophyte

RAUNKIAER [71] LIFE FORM:
Therophyte
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Habitat characteristics

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More info for the terms: competition, density, shrub, shrubs

Foxtail chess and red brome prefer disturbed sites in Mediterranean climates [41,66].  Elevational ranges are described below by state:

Species State Range foxtail chess, red brome California 7,200 feet (2,200 m) [41] red brome Nevada  1,200 to 6,000 feet ( 370-1,800m) [44,48] red brome southern Nevada 4,000 to 5,000 feet (1,200-1,500 m) [10] red brome Utah 3,000 to 5,000 feet (910-1,520 m) [64]

Regional: In California, foxtail chess prefers areas receiving less than 9.8 inches (250 mm) annual rainfall [8]. Foxtail chess is a dominant species in California valley grasslands receiving less than 7.5 inches (190 mm) rainfall [40], and is abundant in California valley grasslands receiving less than 12 inches (305 mm) annual precipitation. In areas with annual precipitation greater than 12 inches (305 m), foxtail chess is replaced by soft chess (Bromus mollis) [7,8]. 

Bowers [19] monitored the relative abundance of northern Mojave Desert annuals over 6 years in relation to precipitation. Red brome density was highest during years receiving 2.4 to 4.2 inches (63-109 mm) precipitation; results are summarized below:

Pre-census precipitation (mm) between 1970-1976:

Year Sept.-Oct. Nov.-Dec. Jan.-Feb. Total Mean red brome/0.25m2 1971 0 37.4 8.1 45.5  0.1131972 0 41.4 0 41.4  0.132 1973 40.4 29.7 70.9 141.0  0.073 1974 3.8 24.9 35.0 63.7  0.959 1975 25.9 35.3 5.1 66.3  1.012 1976 5.8 4.8 98.0 108.6  6.780
Soils: Red brome commonly occurs in small patches on shallow soils, growing best where there is little competition from other annuals [86]. In southern Nevada, red brome occupies blackbrush communities with coarse-textured soils, showing best growth under shrubs and peripheries of shrub canopies [10]. Upland clay and sandy loam ranges and rolling sandy hills receiving 8 to 12 inches (203-305 mm) precipitation promote good growth in southern Utah 60.

Red brome is often found in areas with relatively high levels of sulfur dioxide pollution [69].
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Habitat: Cover Types

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This species is known to occur in association with the following cover types (as classified by the Society of American Foresters):

More info for the term: cover

SAF COVER TYPES [33]:




242 Mesquite

249 Canyon live oak

250 Blue oak-foothills pine

255 California coast live oak
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Habitat: Plant Associations

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This species is known to occur in association with the following plant community types (as classified by Küchler 1964):

More info for the term: shrub

KUCHLER [56] PLANT ASSOCIATIONS:




K027 Mesquite bosques

K030 California oakwoods

K033 Chaparral

K035 Coastal sagebrush

K038 Great Basin sagebrush

K039 Blackbrush

K041 Creosotebush

K042 Creosotebush-bursage

K043 Paloverde-cactus shrub

K044 Creosotebush-tarbush
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Habitat: Rangeland Cover Types

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This species is known to occur in association with the following Rangeland Cover Types (as classified by the Society for Range Management, SRM):

More info for the terms: cover, grassland, shrub, shrubland, woodland

SRM (RANGELAND) COVER TYPES [74]:




201 Blue oak woodland

202 Coast live oak woodland

205 Coastal sage shrub

206 Chamise chaparral

207 Scrub oak mixed chaparral

208 Ceanothus mixed chaparral

209 Montane shrubland

210 Bitterbrush

211 Creosotebush scrub

212 Blackbush

214 Coastal prairie

215 Valley grassland

401 Basin big sagebrush

413 Gambel oak

414 Salt desert shrub

503 Arizona chaparral

506 Creosotebush-bursage

507 Palo verde-cactus
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Immediate Effect of Fire

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Fire kills foxtail chess and red brome [34].
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Importance to Livestock and Wildlife

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In general, foxtail chess and red brome are of little value to livestock and big game. The long awns of red brome are harmful to livestock when seeds are ripe [43]. Under some circumstances, red brome may provide a source of forage. Krausman and others [55] observed light desert mule deer use (< 1% of seasonal diet) of red brome in Arizona. Desert bighorn sheep also use red brome [73].

Desert cottontail prefer red brome. Heaviest use occurs in winter [79].
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Life Form

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More info for the term: graminoid

Graminoid
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Management considerations

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More info for the terms: shrub, shrubs

Red brome is common in open canopies of Arizona chaparral subjected to heavy grazing [18].
Betancout [13] attributes red brome expansion in the Upper
Sonoran Desert of central and southern Arizona to climate change. Since 1976, increased winter precipitation has promoted the
spread of red brome.
In relatively dry areas of the Southwest, red brome may displace native species during wetter years [4,14,44].
Relatively drier winters and wetter summers may slow the red brome invasion [13].



The smut Ustilago bullata is common on red brome in Nevada. Infected plants produce
fewer viable seeds than uninfected plants [44].



In California chaparral, fall germination of foxtail chess gives the grass a competitive
advantage over shrub seedlings, which usually germinate in spring [15].
Foxtail chess competes with California sagebrush (Artemisia californica)
seedlings during their 1st growing season. Planting shrubs that are 1 or more
years old increases their competitive ability against red brome [31]. Bartolome and others [8] found mulch 
provided no significant (p > 0.05) benefit to standing crops foxtail
chess in
areas of California receiving less than 9.8 inches (250 mm) annual precipitation.



Foxtail chess is an annual weed in California cereal crops [28].
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Nutritional Value

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The calcium:phosphorous ratio for red brome is 1:2 [37].



Seegmiller and others [73] conducted a nutritional analysis of red brome within the Harlequin Mountains, Arizona. Red
brome parts selected for analysis (leaves, flowers, new growth) were those used by desert bighorn sheep. Results (mean %)
are presented below:






Dry Matter 
Protein 
Lignin 
Cellulose 
Cell Solubles 
Hemicellulose 
Ether Extract 
Ash 

January-February
36.17
11.29
8.63
24.24
40.21
20.12
2.32
13.94

March-April
36.51
5.80
5.06
28.70
34.25
26.64
1.89
7.66

May-June
97.72
3.32
6.58
31.19
24.28
31.16
0.66
10.85

July-August
89.28
4.00
7.45
33.31
23.78
28.47
2.08
11.71
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Palatability

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The palatability of red brome to livestock and
wildlife in Utah has been rated as follows [30]:

Elk Poor
Mule deer Fair
Antelope Fair
Upland game bird Fair
Waterfowl Poor
Small nongame bird Fair
Small mammal Good

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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Plant Response to Fire

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More info for the term: seed

Red brome establishes from on- or off-site seed sources following fire [63].
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Regeneration Processes

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Foxtail chess germinates well under the winter temperature regime of southern California [3]. Sunlight may enhance germination at higher temperatures. Freshly harvested red brome seeds are unable to germinate in the dark at temperatures above 59 degrees Fahrenheit (15 °C), but freshly harvested seeds  usually germinate in the dark at temperatures between 41 and 59 degrees Fahrenheit (5-15 °C). White light inhibits germination even at low irradiance. Dry storage at 68 degrees Fahrenheit (20 °C) removes the inhibitory effects of higher temperatures ( > 68 degrees Fahrenheit (20 °C)), widening the seeds' temperature range for germination and eliminating their sensitivity to light [28].

Red brome germinates at a less exact rainfall and temperature requirement than native species [11]. In general, fall rains promote germination and establishment . In blackbrush communities of southern Nevada, Beatley [10] found red brome germination followed heavy rains (> 1 inch (3 cm)) between October and December. However, germination is not limited to fall and may occur following heavy spring rains. 

Laude [57] evaluated seedling emergence from freshly harvested and stored red brome seeds, which were were planted in a greenhouse setting and monitored for 28 days. Increased storage time increased percent emergence, with germinants achieving 100% emergence in October, 5 months after mid-June seed collection.

High levels of cadmium and nickel impair emergence of red brome [65].
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Regional Distribution in the Western United States

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This species can be found in the following regions of the western United States (according to the Bureau of Land Management classification of Physiographic Regions of the western United States):

BLM PHYSIOGRAPHIC REGIONS [12]:




2 Cascade Mountains

3 Southern Pacific Border

4 Sierra Mountains

5 Columbia Plateau

6 Upper Basin and Range

7 Lower Basin and Range
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Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Successional Status

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More info on this topic.

More info for the terms: presence, seed, succession

The presence of foxtail chess and red brome are closely related to annual precipitation. They are commonly early or mid-seral species where annual precipitation is greater than 9.8 inches (250 mm)  [40].

Red brome is commonly an early to mid-seral species in California chaparral. It is usually sparse in early succession chaparral systems of northern California but may increase rapidly in areas of low soil fertility and moisture [16]. Peak population numbers require several years for seed dispersal into burns or buildup from on-site producers. Continued disturbance such as grazing and repeated low-severity fires favor red brome over native early-seral chaparral species [52]. 

Within blackbrush communities of Nevada, red brome persists in high-density stands for many years [10].

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bibliographic citation
Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Synonyms

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Red brome –

Anisantha madritensis (L.) Nevski [76]

B. madritensis ssp. rubens (L.) Husnot [41,46]
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bibliographic citation
Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Taxonomy

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There is taxonomic disagreement about foxtail chess (Bromus madritensis L.) (Poaceae) in the
strict sense. Following the systematics of several authorities, this report uses the scientific name
Bromus madritensis L. for foxtail chess and Bromus rubens L. for red brome [36,47,49,80,82,83].

Some systematists recognize these entities as subspecies of foxtail chess:
the type subspecies (Bromus madritensis ssp. madritensis) and
red brome (Bromus madritensis ssp. rubens (L.) Husnot) [41,46].
There is consensus that the 2 entities are very closely related [1,84], with both
scientific names used in current literature.



This report considers Bromus madritensis in the broad sense. Studies concerning United States populations
of B. rubens may be interpreted as B. m. ssp. rubens [1,84].
Where possible, distinctions are made between foxtail chess (B. madritensis)
and red brome (B. rubens). The common name foxtail chess is used
when discussing the species as a whole, and when literature cited does not distinguish between
foxtail chess and red brome in areas where their distributions overlap (mostly California).
Red brome refers to B. rubens.
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cc-publicdomain
bibliographic citation
Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. Simonin, Kevin A. 2001. Bromus rubens, Bromus madritensis. In: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.fed.us /database/feis/plants/graminoid/bropum/all.html

Bromus madritensis

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Bromus madritensis is a species of brome grass known by the common name compact brome. The specific epithet madritensis refers to Madrid, Spain. It has a diploid number of 28.

There are two subspecies:

  • Bromus madritensis subsp. madritensis: panicles less dense, stem and leaf sheath less hairy
  • Bromus madritensis subsp. rubens (syn. Bromus rubens) – foxtail brome, foxtail chess, red brome: dense panicles and slightly hairy stems

Description

Reddish subspecies rubens habit

Bromus madritensis is an winter annual grass, growing solitary or tufted, with erect or ascending culms growing 20–70 cm (7.9–27.6 in) high. The leaf sheaths are downy or slightly hairy. The grass lacks auricles and the glabrous ligules are 1.5–2 mm (0.059–0.079 in) long. Its flat leaf blades are either glabrous or slightly hairy, and measure 4–20 cm (1.6–7.9 in) long and 1–5 mm (0.039–0.197 in) wide. The erect and ellipsoid panicles are 3–12 cm (1.2–4.7 in) long and 2–6 cm (0.79–2.36 in) wide, with short branches that ascend and slightly spread. The branches never droop and bear one or two spikelets each. The spikelets are 4–6 cm (1.6–2.4 in) long, longer than the panicle branches, and bear seven to eleven florets. The spikelets vary in color from green to distinctly purplish-red. The lightly hairy glumes taper at their ends and have translucent margins. The lower glumes are one-nerved and 5–10 mm (0.20–0.39 in) long, and the upper glumes are three-nerved and 10–15 mm (0.39–0.59 in) long. The glabrous and slightly rough lemmas are 1.5–2 cm (0.59–0.79 in) long. The lemmas are hairier towards their edges and have five to seven veins. The awns are about the same length, 1.2–2.3 cm (0.47–0.91 in) long, and curve slightly. The anthers are 0.5–1 mm (0.020–0.039 in) long. The caryopses are as long as 11 mm (0.43 in).[2][3]

The grass emerges in early winter and remains dormant until spring when heavy rainfall and higher temperatures stimulate growth. Plants flower from this period typically until May when water stress inhibits the grass. Populations grow during periods of heavy rainfall and populations can be wiped out during extended periods of drought.[4]

The grass alters soil conditions and the competition brought about by the grass both negatively affect native plant populations, and the highly flammable nature of the grass produces wildfires in North American communities where fire was previously rare. Dry florets of the weed entangle themselves in animal hair and can tear at the digestive tracts of foraging livestock.[4]

Habitat and distribution

Bromus madritensis is native to southern and western Europe but has been introduced and naturalized nearly worldwide. In North America it is found primarily in the western United States, in Oregon, California, and Arizona. The grass was brought to North America in 1848 and was naturalized by the 1890s.

In its native range the grass grows in cultivated fields and steppes, and in North America it grows in waste areas, road verges, and disturbed areas, in both ranges primarily on dry stony or sandy soil.[3] In California, the weedy grass occurs in areas disturbed by wildfires. It grows from sea level to elevations of 1,300 m (4,300 ft).[4]

References

  1. ^ "Bromus madritensis". USDA Plants Database. United States Department of Agriculture. Retrieved 22 August 2018.
  2. ^ Merrit Lyndon Fernald (1970). R. C. Rollins (ed.). Gray's Manual of Botany (Eighth (Centennial) – Illustrated ed.). D. Van Nostrand Company. p. 103. ISBN 0-442-22250-5.
  3. ^ a b Flora of North America Editorial Committee (1993). Flora of North America: North of Mexico. Vol. 24. Oxford University Press. p. 226. ISBN 9780195310719.
  4. ^ a b c Carla C. Bossard; John M. Randall; Marc C. Hoshovsky, eds. (2000). Invasive Plants of California's Wildlands (illustrated ed.). University of California Press. p. 74-75. ISBN 9780520225473.
  • Simonin, Kevin A. (2001). "Bromus rubens, Bromus madritensis". Fire Effects Information System (FEIS). US Department of Agriculture (USDA), Forest Service (USFS), Rocky Mountain Research Station, Fire Sciences Laboratory.

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Bromus madritensis: Brief Summary

provided by wikipedia EN

Bromus madritensis is a species of brome grass known by the common name compact brome. The specific epithet madritensis refers to Madrid, Spain. It has a diploid number of 28.

There are two subspecies:

Bromus madritensis subsp. madritensis: panicles less dense, stem and leaf sheath less hairy Bromus madritensis subsp. rubens (syn. Bromus rubens) – foxtail brome, foxtail chess, red brome: dense panicles and slightly hairy stems
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copyright
Wikipedia authors and editors
original
visit source
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wikipedia EN