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Ross' Sedge

Carex rossii Boott

Description

provided by eFloras
Plants densely cespitose; rhizomes usually ascending, occasionally horizontally spreading, dark reddish brown to purplish brown, 0–10 mm, stout. Culms ascending, 7–30(–40) cm, weakly to strongly scabrous distally; bases (remnants of old leaves) slightly fibrous. Leaf blades pale to dark green, usually equaling or exceeding stems, occasionally shorter, 0.8–2.5(–4) mm wide, herbaceous, glabrous abaxially, strongly scabrous to papillose adaxially. Inflorescences with both staminate and pistillate spikes; peduncles of basal pistillate spikes erect, elongate, slender; peduncles of staminate spikes 1.1–10 mm; proximal nonbasal bracts leaflike, exceeding inflorescences. Spikes: proximal pistillate spikes 2–4 (basal spikes 1–2); cauline spikes overlapping or somewhat separated, with 3–10(–15) perigynia; staminate spikes (4.8–)6–12.8 × (0.7–) 0.9–1.3(–2.5) mm. Scales: pistillate scales pale to dark reddish brown, with narrow white margins, ovate, 2.9–5.7 × 1.4–2.3 mm, shorter than perigynia, apex acute or acuminate to long-acuminate; staminate scales lanceolate, 3.2–5.8 × 1.2–1.8 mm, apex acuminate. Anthers 1.2–2 mm. Perigynia green to pale brown, veinless, ellipsoid to obovoid, 3.1–4.5 × 1.4–1.7 mm; beak straight or slightly bent, pale green, occasionally with reddish brown tinge, 0.9–1.7 mm, ciliate-serrulate, apical teeth 0.2–0.4 mm. Stigmas 3. Achenes brown, globose to obovoid or ellipsoid, obtusely trigonous in cross section, 1.9–2.4 × 1.3–1.7 mm. 2n = 36.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 23: 532, 533, 536, 537, 548 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
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partner site
eFloras

Distribution

provided by eFloras
Alta., B.C., Man., N.W.T., Ont., Sask., Yukon; Alaska, Ariz., Calif., Colo., Idaho, Mich., Minn., Mont., Nebr., Nev., N.Mex., Oreg., S.Dak., Utah, Wash., Wyo.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 23: 532, 533, 536, 537, 548 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Flowering/Fruiting

provided by eFloras
Fruiting mid Apr–early Sep.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 23: 532, 533, 536, 537, 548 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Habitat

provided by eFloras
Moist or dry, sandy or rocky, open montane pine, fir, and spruce woodlands, sagebrush slopes, deciduous wooded slopes, prairies, alpine meadows; 210–3700m.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 23: 532, 533, 536, 537, 548 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Synonym

provided by eFloras
Carex deflexa Hornemann var. farwellii Britton; C. deflexa var. media L. H. Bailey; C. deflexa var. rossii (Boott) L. H. Bailey; C. farwellii (Britton) Mackenzie; C. novae-angliae Schweinitz var. rossii (Boott) L. H. Bailey
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 23: 532, 533, 536, 537, 548 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
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: cover, density, duff, fire use, forbs, forest, frequency, fuel, fuel moisture, habitat type, prescribed fire, rhizome, seed, shrubs, stand-replacing fire, succession, wildfire

Ross's sedge is commonly found in both prefire and postfire forest vegetation [101,102,103].
It may also occur on recently burned sites when it is not present in
adjacent, unburned areas [72,73,76], suggesting postfire establishment from the
soil seed bank. Establishment or re-establishment of Ross's sedge occurs quickly,
and it is estimated to take 2 to 10 postfire years for Ross's sedge to return to
prefire abundance (review by [108]). Following the Yellowstone
fires of 1988, Ross's sedge was found in the first 2 postfire years [105],
and Metzger and others [69] described it as "common" or
"abundant" 2 years after a stand-replacing fire in a Wyoming lodgepole pine
forest. Ross's sedge was also common on recent burns (postfire years 1-10) in a
northern boreal forest in Saskatchewan [87]. Following an August wildfire in 1970 in
ponderosa pine and Douglas-fir forests in north-central Washington, where Ross's sedge was
"prominent" in the prefire vegetation, several study areas were fertilized and
seeded with nonnative grasses and forbs [103,104]. Native species,
including Ross's sedge, retained dominance during the first 4 postfire years
(duration of the study period). Ross'ss sedge cover averaged across 4 watersheds
(3 seeded, 1 unseeded) indicated a steady increase from 0.1% in postfire year 1, to
0.7% in postfire year 4 [104].

Studies of the Yellowstone fires of 1988 examined vegetation on burned areas
in the first 3 postfire years. Ross's sedge sprouted from rhizomes following the
fires, and sprout density did not change significantly during the
study period. Ross's sedge sprouts were most abundant in large (500-3600 ha) burned
patches, but were also found in small (1 ha) and moderate-sized (70-200 ha)
patches. Ross's sedge was present in unburned stands and sprouted on sites where
light-surface (soil organic matter largely intact), severe-surface (soil organic
matter completely consumed), and crown fires (canopy needles consumed) had
burned [106].

While Steele and Geier-Hayes [95] suggest that
Ross's sedge may
respond poorly to burning, several studies indicate that it is unchanged or
increases in early postfire succession after prescribed burning. Biomass of
Ross's sedge was significantly (P=0.015) greater on burned (11.4 kg/ha)
vs. unburned (7.2 kg/ha) plots 5 to 6 years after low-severity prescribed spring
underburning in central Oregon ponderosa pine stands. Cover was slightly, but
not significantly, higher on burned sites [17]:

Percent cover of Ross's sedge following
understory burning in ponderosa pine stands, central Oregon [17]
Sample date Burn Control
Preburn 1.0 0.8
Year 2 1.3 0.8
Years 5-6 2.5 1.6

Arno [7,8] found percent cover of
Ross's sedge increased following prescribed
fire treatments on both "wet" and "dry" burns (based on moisture content of duff
and large woody fuels).

Average percent cover by burn treatment for
Ross's sedge in the shelterwood
cutting unit at Lick Creek, Montana [8]
Burn treatment Pretreatment Postfire year 1 Postfire year 2 Postfire year 3 Postfire year 4
No burn 0.5 0.8 0.8 1.1 1.1
Low consumption burn ("wet burn") 0.7 1.3 1.9 1.9 2.1
High consumption burn ("dry burn") 0.5 1.3 2.0 2.9 2.7

Effects of timber harvest and prescribed fire: Ross's sedge tends to increase after
timber harvest, particularly after burning of postharvest residue [85,89,96,115,116].
Prescribed burning of shelterwood-harvested units in northern and central
Idaho mixed conifer stands compared "moist" and "dry" burns, based primarily on
fuel moisture content (duff moisture ~90% and ~40%, respectively) and on season
of burning (spring and fall, respectively). Ross's sedge increased on these sites through
a combination of seedling establishment and rhizome stimulation
following shelterwood cutting with and without prescribed burning [89].

Percent cover of Ross's sedge following understory
burning in northern and central Idaho shelterwood-harvest units [89]
Site Sample date No burn Spring "moist" burn
(duff moisture
~90%; 15%-30% duff consumed) Fall "dry" burn
(duff moisture ~40%; 43%-90% duff consumed)
Northern ID mixed conifer Preburn 0.7 0.5 0.7
Postfire year 1 1.3 2.5 3.9
Central ID ponderosa pine
Preburn 0.0 0.1 0.3
Postfire year 1 1.3 --* 1.3
Postfire year 2 -- -- --
Postfire year 3 3.6 8.4 6.6
Postfire year 5 -- -- --
Postfire year 6 6.8 -- 11.2
*-- indicates data were not collected on that site on those dates


Clearcutting in a grand fir-Oregon boxwood (Abies grandis-Paxistima myrsinites)
habitat type of north-central Idaho followed by broadcast burning of harvest residue found
Ross's sedge was prevalent on all sites in the 1-year age class, though it was dominant
in the understory of only 2 of the 10 stands. After 3 years, percent cover of
Ross's sedge
in stands increased 2 to 10 times that of first year coverage. Frequency changed little,
however, indicating the increase in cover was not the result of new recruitment.
The vegetation trend over the first 3 years was toward Ross's sedge dominance. By
year 8, dominance of Ross's sedge was decreasing, with shrubs becoming dominant
on most sites, though Ross's sedge may continue to dominate on drier, low elevation sites.
Ross's sedge was rare on sites 23 years after clearcutting and burning [115,116].
A study by Metlen and others [68] in ponderosa pine/Douglas-fir stands in Montana found that
Ross's sedge showed no response to either thinning treatments or burn treatments;
however, it increased following a combination of thinning and burning. For more
information on this study, see the Research Project Summary.

Lyon's Research Paper
also provides information on prescribed fire use and postfire response of plant
species including Ross's sedge.
license
cc-publicdomain
bibliographic citation
Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Common Names

provided by Fire Effects Information System Plants
Ross's sedge
license
cc-publicdomain
bibliographic citation
Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Conservation Status

provided by Fire Effects Information System Plants
Information on state-level protected status of plants in the United States is available at Plants Database.
license
cc-publicdomain
bibliographic citation
Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Description

provided by Fire Effects Information System Plants
More info for the terms: achene, fruit, grassland, hemicryptophyte

This description provides characteristics that may be relevant to fire ecology, and is not meant for identification. Keys for identification are available (e.g., [29,30,43,45,49,51]).

Ross'ss sedge is a long-lived, cespitose perennial with dense, medium-sized clumps [20,23,36,39,43,45,47,49,51,62,74]. Where dominant in grassland associations, Ross's sedge can form mats 0.3 to 3 feet (0.1-1 m) across [79]. Culms grow 2 to 15 inches (5-40 cm) tall [36,39,43,45,47,51,62,74,93] with high, slender, erect stems [51,62]. Ross's sedge has several basal leaves, 1 to 4 mm wide and as long as or longer than stems [23,47,49,62,74].

Ross's sedge bears a terminal inflorescence of 1 to 4 apical staminate spikes [47,49,74] 3 to 15 mm long [23,36,93]. Borne near the staminate spikes are 1 to 5 shorter, lateral, few-flowered pistillate spikes 3 to 4.5 mm long [23,36,43,47,49,74,111]. Some plants have shorter culms (0.4-2 inches (1-5 cm)) bearing mostly pistillate spikes, while others have taller culms (2-12 inches (5-30 cm)) bearing both staminate and pistillate spikes [29,30]. Fruit is a 3-sided achene 2 to 5 mm long [47,74].

Ross's sedge is a shallow-rooted (top 2 inches (5 cm) of soil) [35] hemicryptophyte [20]. Most authors agree that Ross's sedge has short, horizontal or ascending stolons or rhizomes [36,39,47,51,74,93]. Others describe Ross's sedge as occurring with and without rhizomes [23,111] or as non-rhizomatous [57,95].

license
cc-publicdomain
bibliographic citation
Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Distribution

provided by Fire Effects Information System Plants

Ross's sedge occurs from Alaska east to Nunavut and south through the western United States to California, Arizona, and New Mexico [23,30,39,41,43,45,47,49,51,52,53,74,84,93,110,111]. It is also common in the Dakotas and Minnesota [29,36,48,52] and occurs rarely in Ontario, Michigan, and Nebraska [36,40,41,52,109].

Flora of North America provides a distributional map of Ross's sedge.

license
cc-publicdomain
bibliographic citation
Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Fire Ecology

provided by Fire Effects Information System Plants
More info for the terms: cover, duff, fire regime, forest, frequency, grassland, litter, low-severity fire, mesic, natural, potential natural vegetation, potential natural vegetation group, rhizome, seed, shrub, shrubland, shrubs, woodland

Fire adaptations: Ross's sedge is a residual colonizer after fire [99] and has been described as fire-resistant [47,74,77,108], defined as having a greater than 65% chance that at least half of the population will survive or reestablish after fire [108]. It often increases after fires that do not consume the litter and duff layer or cause excessive soil heating [77,91,96]. Ross's sedge regenerates after fire from surviving rhizomes [15,16,32,77,91,96], approaching preburn coverage within 1 to 2 years [47,74]. Ross's sedge also reestablishes from seed stored in the duff and soil [77,91,96] that is stimulated by soil heating [15,16,32,50,63,91]. Even when Ross's sedge is not present in prefire vegetation, viable seed can remain stored in the soil until fire creates conditions favorable for germination [10].

FIRE REGIMES: Ross's sedge is present in many different plant communities across a large portion of the United States. As a widespread understory species, it is subject to a wide range of FIRE REGIMES, and it is neither eliminated by fire nor dependent on fire. Frequent fires may increase frequency and cover of Ross's sedge due to increased vigor, rhizome extension, and seedling establishment following fire [10,61,108], and by creating openings and reducing shade.

The following table provides fire regime information that may be relevant to Ross's sedge. Find further fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find FIRE REGIMES".

Fire regime information on vegetation communities in which Ross's sedge may occur. For each community, fire regime characteristics are taken from the LANDFIRE Rapid Assessment Vegetation Models [59]. These vegetation models were developed by local experts using available literature, local data, and/or expert opinion as documented in the PDF file linked from each Potential Natural Vegetation Group listed below. Cells are blank where information is not available in the Rapid Assessment Vegetation Model. Pacific Northwest California Southwest Great Basin Northern Rockies Northern Great Plains Great Lakes Pacific Northwest Vegetation Community (Potential Natural Vegetation Group) Fire severity* Fire regime characteristics Percent of fires Mean interval
(years) Minimum interval
(years) Maximum interval
(years) Northwest Grassland Bluebunch wheatgrass Replacement 47% 18 5 20 Mixed 53% 16 5 20 Idaho fescue grasslands Replacement 76% 40     Mixed 24% 125     Alpine and subalpine meadows and grasslands Replacement 68% 350 200 500 Mixed 32% 750 500 >1,000 Northwest Shrubland Mountain big sagebrush (cool sagebrush) Replacement 100% 20 10 40 Northwest Woodland Western juniper (pumice) Replacement 33% >1,000     Mixed 67% 500     Pine savannah (ultramafic) Replacement 7% 200 100 300 Surface or low 93% 15 10 20 Ponderosa pine Replacement 5% 200     Mixed 17% 60     Surface or low 78% 13     Subalpine woodland Replacement 21% 300 200 400 Mixed 79% 80 35 120 Northwest Forested Ponderosa pine (xeric) Replacement 37% 130     Mixed 48% 100     Surface or low 16% 300     Dry ponderosa pine (mesic) Replacement 5% 125     Mixed 13% 50     Surface or low 82% 8     Mixed conifer (southwestern Oregon) Replacement 4% 400     Mixed 29% 50     Surface or low 67% 22     California mixed evergreen (northern California) Replacement 6% 150 100 200 Mixed 29% 33 15 50 Surface or low 64% 15 5 30 Lodgepole pine (pumice soils) Replacement 78% 125 65 200 Mixed 22% 450 45 85 Subalpine fir Replacement 81% 185 150 300 Mixed 19% 800 500 >1,000 Mixed conifer (eastside dry) Replacement 14% 115 70 200 Mixed 21% 75 70 175 Surface or low 64% 25 20 25 Mixed conifer (eastside mesic) Replacement 35% 200     Mixed 47% 150     Surface or low 18% 400     Red fir Replacement 20% 400 150 400 Mixed 80% 100 80 130 Spruce-fir Replacement 84% 135 80 270 Mixed 16% 700 285 >1,000 California Vegetation Community (Potential Natural Vegetation Group) Fire severity* Fire regime characteristics Percent of fires Mean interval
(years) Minimum interval
(years) Maximum interval
(years) California Grassland Alpine meadows and barrens Replacement 100% 200 200 400 California Shrubland Montane chaparral Replacement 34% 95     Mixed 66% 50     California Woodland Ponderosa pine Replacement 5% 200     Mixed 17% 60     Surface or low 78% 13     California Forested Mixed conifer (North Slopes) Replacement 5% 250     Mixed 7% 200     Surface or low 88% 15 10 40 Mixed conifer (South Slopes) Replacement 4% 200     Mixed 16% 50     Surface or low 80% 10     Aspen with conifer Replacement 24% 155 50 300 Mixed 15% 240     Surface or low 61% 60     Jeffrey pine Replacement 9% 250     Mixed 17% 130     Surface or low 74% 30     Interior white fir (northeastern California) Replacement 47% 145     Mixed 32% 210     Surface or low 21% 325     Red fir-white fir Replacement 13% 200 125 500 Mixed 36% 70     Surface or low 51% 50 15 50 Red fir-western white pine Replacement 16% 250     Mixed 65% 60 25 80 Surface or low 19% 200     Sierra Nevada lodgepole pine (cold wet upper montane) Replacement 23% 150 37 764 Mixed 70% 50     Surface or low 7% 500     Sierra Nevada lodgepole pine (dry subalpine) Replacement 11% 250 31 500 Mixed 45% 60 31 350 Surface or low 45% 60 9 350 Southwest Vegetation Community (Potential Natural Vegetation Group) Fire severity* Fire regime characteristics Percent of fires Mean interval
(years) Minimum interval
(years) Maximum interval
(years) Southwest Grassland Montane and subalpine grasslands Replacement 55% 18 10 100 Surface or low 45% 22     Montane and subalpine grasslands with shrubs or trees Replacement 30% 70 10 100 Surface or low 70% 30     Southwest Shrubland Mountain sagebrush (cool sage) Replacement 75% 100     Mixed 25% 300     Gambel oak Replacement 75% 50     Mixed 25% 150     Mountain-mahogany shrubland Replacement 73% 75     Mixed 27% 200     Southwest Woodland Pinyon-juniper (mixed fire regime) Replacement 29% 430     Mixed 65% 192     Surface or low 6% >1,000     Pinyon-juniper (rare replacement fire regime) Replacement 76% 526     Mixed 20% >1,000     Surface or low 4% >1,000     Ponderosa pine/grassland (Southwest) Replacement 3% 300     Surface or low 97% 10     Bristlecone-limber pine (Southwest) Replacement 67% 500     Surface or low 33% >1,000     Southwest Forested Ponderosa pine-Gambel oak (southern Rockies and Southwest) Replacement 8% 300     Surface or low 92% 25 10 30 Ponderosa pine-Douglas-fir (southern Rockies) Replacement 15% 460     Mixed 43% 160     Surface or low 43% 160     Southwest mixed conifer (warm, dry with aspen) Replacement 7% 300     Mixed 13% 150 80 200 Surface or low 80% 25 2 70 Southwest mixed conifer (cool, moist with aspen) Replacement 29% 200 80 200 Mixed 35% 165 35   Surface or low 36% 160 10   Aspen with spruce-fir Replacement 38% 75 40 90 Mixed 38% 75 40   Surface or low 23% 125 30 250 Stable aspen without conifers Replacement 81% 150 50 300 Surface or low 19% 650 600 >1,000 Lodgepole pine (Central Rocky Mountains, infrequent fire) Replacement 82% 300 250 500 Surface or low 18% >1,000 >1,000 >1,000 Spruce-fir Replacement 96% 210 150   Mixed 4% >1,000 35 >1,000 Great Basin Vegetation Community (Potential Natural Vegetation Group) Fire severity* Fire regime characteristics Percent of fires Mean interval
(years) Minimum interval
(years) Maximum interval
(years) Great Basin Grassland Mountain meadow (mesic to dry) Replacement 66% 31 15 45 Mixed 34% 59 30 90 Great Basin Shrubland Mountain big sagebrush Replacement 100% 48 15 100 Mountain big sagebrush with conifers Replacement 100% 49 15 100 Mountain sagebrush (cool sage) Replacement 75% 100     Mixed 25% 300     Montane chaparral Replacement 37% 93     Mixed 63% 54     Gambel oak Replacement 75% 50     Mixed 25% 150     Mountain shrubland with trees Replacement 22% 105 100 200 Mixed 78% 29 25 100 Curlleaf mountain-mahogany Replacement 31% 250 100 500 Mixed 37% 212 50   Surface or low 31% 250 50   Great Basin Woodland Juniper and pinyon-juniper steppe woodland Replacement 20% 333 100 >1,000 Mixed 31% 217 100 >1,000 Surface or low 49% 135 100   Ponderosa pine Replacement 5% 200     Mixed 17% 60     Surface or low 78% 13     Great Basin Forested Interior ponderosa pine Replacement 5% 161   800 Mixed 10% 80 50 80 Surface or low 86% 9 8 10 Ponderosa pine-Douglas-fir Replacement 10% 250   >1,000 Mixed 51% 50 50 130 Surface or low 39% 65 15   Great Basin Douglas-fir (dry) Replacement 12% 90   600 Mixed 14% 76 45   Surface or low 75% 14 10 50 Aspen with conifer (low to midelevation) Replacement 53% 61 20   Mixed 24% 137 10   Surface or low 23% 143 10   Douglas-fir (warm mesic interior) Replacement 28% 170 80 400 Mixed 72% 65 50 250 Aspen with conifer (high elevation) Replacement 47% 76 40   Mixed 18% 196 10   Surface or low 35% 100 10   Stable aspen-cottonwood, no conifers Replacement 31% 96 50 300 Surface or low 69% 44 20 60 Spruce-fir-pine (subalpine) Replacement 98% 217 75 300 Mixed 2% >1,000     Aspen with spruce-fir Replacement 38% 75 40 90 Mixed 38% 75 40   Surface or low 23% 125 30 250 Stable aspen without conifers Replacement 81% 150 50 300 Surface or low 19% 650 600 >1,000 Northern Rockies Vegetation Community (Potential Natural Vegetation Group) Fire severity* Fire regime characteristics Percent of fires Mean interval
(years) Minimum interval
(years) Maximum interval
(years) Northern Rockies Grassland Mountain grassland Replacement 60% 20 10   Mixed 40% 30     Northern Rockies Shrubland Mountain shrub, nonsagebrush Replacement 80% 100 20 150 Mixed 20% 400     Mountain big sagebrush steppe and shrubland Replacement 100% 70 30 200 Northern Rockies Woodland Ancient juniper Replacement 100% 750 200 >1,000 Northern Rockies Forested Ponderosa pine (Northern Great Plains) Replacement 5% 300     Mixed 20% 75     Surface or low 75% 20 10 40 Ponderosa pine (Northern and Central Rockies) Replacement 4% 300 100 >1,000 Mixed 19% 60 50 200 Surface or low 77% 15 3 30 Ponderosa pine (Black Hills, low elevation) Replacement 7% 300 200 400 Mixed 21% 100 50 400 Surface or low 71% 30 5 50 Ponderosa pine (Black Hills, high elevation) Replacement 12% 300     Mixed 18% 200     Surface or low 71% 50     Ponderosa pine-Douglas-fir Replacement 10% 250   >1,000 Mixed 51% 50 50 130 Surface or low 39% 65 15   Douglas-fir (xeric interior) Replacement 12% 165 100 300 Mixed 19% 100 30 100 Surface or low 69% 28 15 40 Douglas-fir (warm mesic interior) Replacement 28% 170 80 400 Mixed 72% 65 50 250 Douglas-fir (cold) Replacement 31% 145 75 250 Mixed 69% 65 35 150 Grand fir-Douglas-fir-western larch mix Replacement 29% 150 100 200 Mixed 71% 60 3 75 Western larch-lodgepole pine-Douglas-fir Replacement 33% 200 50 250 Mixed 67% 100 20 140 Grand fir-lodgepole pine-larch-Douglas-fir Replacement 31% 220 50 250 Mixed 69% 100 35 150 Persistent lodgepole pine Replacement 89% 450 300 600 Mixed 11% >1,000     Whitebark pine-lodgepole pine (upper subalpine, Northern and Central Rockies) Replacement 38% 360     Mixed 62% 225     Lower subalpine lodgepole pine Replacement 73% 170 50 200 Mixed 27% 450 40 500 Lower subalpine (Wyoming and Central Rockies) Replacement 100% 175 30 300 Upper subalpine spruce-fir (Central Rockies) Replacement 100% 300 100 600 Northern Great Plains Vegetation Community (Potential Natural Vegetation Group) Fire severity* Fire regime characteristics Percent of fires Mean interval
(years) Minimum interval
(years) Maximum interval
(years) Northern Plains Woodland Oak woodland Replacement 2% 450     Surface or low 98% 7.5 Northern Great Plains wooded draws and ravines Replacement 38% 45 30 100 Mixed 18% 94     Surface or low 43% 40 10   Great Lakes Vegetation Community (Potential Natural Vegetation Group) Fire severity* Fire regime characteristics Percent of fires Mean interval
(years) Minimum interval
(years) Maximum interval
(years) Great Lakes Woodland Great Lakes pine barrens Replacement 8% 41 10 80 Mixed 9% 36 10 80 Surface or low 83% 4 1 20 Jack pine-open lands (frequent fire-return interval) Replacement 83% 26 10 100 Mixed 17% 125 10   Great Lakes Forested Great Lakes pine forest, jack pine Replacement 67% 50     Mixed 23% 143     Surface or low 10% 333 Pine-oak Replacement 19% 357     Surface or low 81% 85     Red pine-white pine (frequent fire) Replacement 38% 56     Mixed 36% 60     Surface or low 26% 84     Red pine-white pine (less frequent fire) Replacement 30% 166     Mixed 47% 105     Surface or low 23% 220     *Fire Severities:
Replacement=Any fire that causes greater than 75% top removal of a vegetation-fuel type, resulting in general replacement of existing vegetation; may or may not cause a lethal effect on the plants.
Mixed=Any fire burning more than 5% of an area that does not qualify as a replacement, surface, or low-severity fire; includes mosaic and other fires that are intermediate in effects.
Surface or low=Any fire that causes less than 25% upper layer replacement and/or removal in a vegetation-fuel class but burns 5% or more of the area [38,58].
license
cc-publicdomain
bibliographic citation
Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Fire Management Considerations

provided by Fire Effects Information System Plants
More info for the terms: cover, seed, severity, succession

In areas where Ross's sedge occurs or has occurred in the past, it typically persists or establishes on burned sites after both prescribed burns and wildfires. Ross's sedge sprouts and may also establish from the soil seed bank after fire. It is likely to remain unchanged or increase in biomass and cover in early postfire succession after fires of any severity. Ross's sedge is likely to remain unchanged or increase after timber harvest with or without fire. However, prescribed burning after harvest is more likely to increase percent cover of Ross's sedge.
license
cc-publicdomain
bibliographic citation
Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Growth Form (according to Raunkiær Life-form classification)

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More info on this topic.

More info for the terms: geophyte, hemicryptophyte

RAUNKIAER [81] LIFE FORM:
Hemicryptophyte
Geophyte
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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Habitat characteristics

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More info for the term: forest

Ross's sedge has high winter hardiness [39] and is found in boreal, temperate, cool semi-arid, and cool mesothermal climates. The occurrence of Ross's sedge increases with increasing continentality and decreases with increasing precipitation [54]. With "very high" drought tolerance [39], Ross's sedge prefers dry sites [39,54,116] and may be considered characteristic of moisture deficient sites [54]. In the Pacific Northwest, Ross's sedge also grows on moist slopes [45,92].

Ross's sedge is common in moist to dry forests [5,43,45,82,110,111], open woods [29,30,41], grasslands [62,79,80], and meadows [14,27,29,30,41,43,45,82,111] in the western portion of its range. It is often found on rocky slopes, unstable screes, and steep banks [39,49,82]. Ross's sedge is common in open woodlands of the northern plains [36], while in Michigan, it grows on sandy or rocky bluffs and windswept crests [40,109].

Ross's sedge prefers well-drained [39,82], moderately dry to very dry, nitrogen-medium soils [54]. Soil textures range from sandy loam to clay loam. Ross's sedge can tolerate excessive soil compaction as well as unstable slopes. Ross's sedge will tolerate mildly saline soils and mildly alkaline to moderately acidic soils [39].

Ross's sedge grows on gentle to steep slopes [22]. The elevational occurrence of Ross's sedge ranges from near sea level to near timberline in the Pacific Northwest [45], and from submontane to subalpine and alpine sites in the Rocky Mountains [54,62,79,80,82,110,111].

Examples of elevation ranges for Ross's sedge by state State Elevation California up to 12,500 feet
(3,800 m) [43,83] Colorado 5,800 to 11,500 feet
(1,770-3,500 m) [4,84] Idaho 7,400 to 10,500 feet
(2,250-3,200 m) [4,94] Nevada 7,000 to 10,500 feet
(2,130-3,200 m) [4,70] Utah 4,400 to 11,300 feet
(1,340-3,445 m) [4,67,70,111,113] Wyoming 6,500 to 10,500 feet
(1,980-3,200 m) [4,5,22,94] Washington
(Mt. Rainier National Park) 3,500 to 6,500 feet
(1,070-1,980 m) [92]

The occurrence of Ross's sedge may decrease at higher elevations where snow persists longer into the growing season. A study in a Wyoming subalpine forest (elevation 10,000 feet (3,050 m)) found little or no Ross's sedge on sites where snow persisted past June 27 [55].

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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Immediate Effect of Fire

provided by Fire Effects Information System Plants
Ross's sedge is top-killed by fire [15,16,47,83].
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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Importance to Livestock and Wildlife

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More info for the terms: cover, forest

Ross's sedge is important summer elk forage, particularly in the first half of the growing season [14,56,65]. Grizzly bears also eat Ross's sedge [25] , and sedges (Carex spp.) are often important winter forage for mountain goats [1].

Palatability/nutritional value: Ross's sedge may be a poor to good forage plant depending on the site [39,62]. Palatability of Ross's sedge has been rated "fair" for domestic sheep, horses, cattle, and small mammals. It has been rated "good" for elk and "poor" for mule deer, white-tailed deer, and pronghorn [28].

In a study of seasonal nutrition trends in Oregon, grasses such as Thurber needlegrass (Achnatherum thurberianum), bottlebrush squirreltail (Elymus elymoides), Sandberg bluegrass (Poa secunda), Idaho fescue (Festuca idahoensis), and prairie Junegrass (Koeleria macrantha) exceed Ross's sedge in protein, phosphorus, calcium, crude fat, and apparent digestibility in early spring. Crude fiber is high in March for Ross's sedge. As the growing season progresses through summer and into fall, Ross's sedge nutritional value increases to surpass the grasses in protein, calcium, crude fat, and apparent digestibility [44]. A Wenatchee National Forest, Washington study found oven-dry crude protein production of Ross's sedge ranged from 0 to 3.9 pounds per acre (4.4 kg/ha). This study also found that crude protein production of Ross's sedge on burned sites was more than double the production on unburned sites [14].

Cover value: Dittberner and Olson [28] rate Ross's sedge cover as poor for large game and fair for nongame birds and small mammals.

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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Key Plant Community Associations

provided by Fire Effects Information System Plants
More info for the terms: association, cover, forest, grassland, habitat type, phase, xeric

Ross's sedge forms dry grassland associations [79] and is a common
aspen parkland [39] and forest understory sedge [47].
Where Ross's sedge dominates the understory, total understory cover may be sparse [3,42].
In north-central Colorado, cover of Ross's sedge is 7% to 16% in ponderosa pine
(Pinus ponderosa)/Ross's sedge habitat types and 4% to 5% in Douglas-fir
(Pseudotsuga menziesii)/Ross's sedge habitat types [42]. Peet [75]
also described limber pine (Pinus flexilis) forests and Rocky Mountain
lodgepole pine (Pinus contorta var. latifolia) forests where
Ross's
sedge is common in the understory, but understory vegetation has little cover.


Vegetation classifications describing plant communities where Ross's sedge is
a dominant species follow:



Colorado:

  • xeric ponderosa pine forests [75]

  • ponderosa pine/true mountain-mahogany (Cercocarpus montanus)/Ross's
    sedge plant association

  • Ross's sedge subalpine turf plant association [11]

  • ponderosa pine/Ross's sedge habitat type [2,4,42]

  • Douglas-fir/Ross's sedge habitat type [4,42]



Idaho:

  • grand fir (Abies grandis)/big huckleberry (Vaccinium membranaceum)
    habitat type; Ross's sedge layer group [95]

  • subalpine fir (Abies lasiocarpa)/Ross's sedge habitat type [4,4,94]

  • whitebark pine (Pinus albicaulis)/Ross's sedge habitat type

  • lodgepole pine/Ross's sedge community type [94]




Nevada:

  • quaking aspen/Ross's sedge forest

  • quaking aspen/mountain snowberry (Symphoricarpos oreophilus)/Ross's sedge
    forest [71]

  • quaking aspen (Populus tremuloides)-subalpine fir/Ross's sedge community type

  • quaking aspen/Ross's sedge community type [4,70]



Oregon:

  • ponderosa pine/antelope bitterbrush (Purshia tridentata)/Idaho fescue (Festuca idahoensis)
    ecosystem: Ross's sedge phase [26]

  • big sagebrush (Artemisia tridentata)/bunchgrass plant association [46]

  • ponderosa pine/antelope bitterbrush/Ross's sedge community type [34,37,78]

  • ponderosa pine-white fir (Abies concolor)/Ross's sedge community type

  • Ross's sedge community type [34]



Utah:

  • subalpine fir/Ross's sedge habitat type [2,4,113]

  • lodgepole pine/Ross's sedge habitat type [2,67]

  • quaking aspen-subalpine fir/Ross's sedge community type

  • quaking aspen/Ross's sedge community type [4,70]




Wyoming:

  • Ross's avens (Geum rossii)/Ross's sedge plant association

  • subalpine fir-Engelmann spruce (Picea engelmannii)/Ross's sedge
    plant association [82]

  • ponderosa pine/Ross's sedge habitat type [3,4,5,86]

  • lodgepole pine/Ross's sedge habitat type [2,3,5]

  • subalpine fir/Ross's sedge habitat type [2,3,4,94]

  • whitebark pine/Ross's sedge habitat type [3,4,94]

  • quaking aspen/mountain snowberry-Ross's sedge habitat type [4]

  • lodgepole pine/Ross's sedge community type [3,22,94]

  • subalpine fir-lodgepole pine/Ross's sedge community type [86]

  • whitebark pine-lodgepole pine/Ross's sedge community type [22]



Intermountain region:

  • quaking aspen/mountain snowberry-Ross's sedge habitat type [4]



Rocky Mountain region:

  • quaking aspen/mountain snowberry-Ross's sedge habitat type [4]

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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Life Form

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More info for the term: graminoid

Graminoid
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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Management considerations

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More info for the terms: cover, forest, scarification

Ross's sedge productivity increases when ponderosa pine stands are thinned [12].
A study of clearcutting in a Colorado subalpine forest found Ross's sedge present
on sites both before and after logging operations. Data were presented
for sedges in general, and on some sites sedge cover significantly (P=0.05)
increased in the 5 years after logging [24].
Ross's sedge often invades
sites or increases in coverage following mechanical scarification [9,66,77].
However, Ross's sedge may also be susceptible to damage during logging operations
because rhizomes can be displaced by log skidding [35].

Cole's [20] study of trampling and vegetation response
found that Ross's sedge was resistant to trampling, primarily
due to its cespitose growth form. The low matting habit and extensive
root system may allow Ross's sedge to withstand
moderate to severe grazing pressure [39].

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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Phenology

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More info on this topic.

Growth of Ross's sedge begins in spring. Flowering occurs during May and June [28].
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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Plant Response to Fire

provided by Fire Effects Information System Plants
More info for the terms: duff, frequency

Ross's sedge sprouts from surviving rhizomes following fire [15,16,108] and is capable of responding rapidly to disturbance [17,69]: Regeneration to preburn levels can occur within 1 to 2 years [47]. Increased coverage of Ross's sedge occurs after most fires severe enough to heat but not completely consume the duff layer [9,13,15,16,32,50,50]. Ross's sedge frequency may also increase after fire [61].
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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Post-fire Regeneration

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More info for the terms: graminoid, ground residual colonizer, herb, rhizome, secondary colonizer, seed, tussock

POSTFIRE REGENERATION STRATEGY [98]:
Rhizomatous herb, rhizome in soil
Tussock graminoid
Ground residual colonizer (on site, initial community)
Secondary colonizer (on-site or off-site seed sources)
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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Regeneration Processes

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More info for the terms: monoecious, scarification, seed

Ross's sedge regenerates from seed and rhizomes [39,108].

Pollination: No information is available on this topic.

Breeding system: Ross's sedge is monoecious [23,36,43,47,49,74,111].

Seed production: No information is available on this topic.

Seed dispersal: Ross's sedge has heavy seed [108] with no long-distance seed dispersal [57].

Seed banking: Ross's sedge has soil-stored seed with long-term viability [63,64,95,97,98]. A study of seed banks in Yellowstone National Park found Ross's sedge present in densities greater than 100 seeds/m² [18]. Seed banks studied in central Idaho found Ross's sedge seed stored in soil of 38 out of 48 forested plots. Seeds were found at depths of 0 to 25 inches (0-10 cm) with overall seed viability of 51% [57].

Germination: No information is available on this topic.

Seedling establishment/growth: No information is available on this topic.

Vegetative regeneration: Ross's sedge regenerates from short horizontal or ascending rhizomes following disturbance [39,108]. According to Garrison and Rummell [35], however, the rhizomes are regenerative only when attached to a living plant; once severed they die. According to Steele and Geier-Hayes [95], Ross's sedge is nonrhizomatous, and "sprouts readily following scarification but responds poorly to burning" [95].

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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Successional Status

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More info for the terms: association, climax, cover, forb, forest, grassland, presence, seed, stand-replacing fire, wildfire

Ross's sedge is generally considered an early-seral species on disturbed sites [6,31,57,66,69,79,90,96,114] and has been described as an "aggressive pioneer" [39]. However, Ross's sedge is also found in developed or climax forest communities [2,4,19]. For example, Turner and others [106] described Ross's sedge in a 130 year-old lodgepole pine stand in Yellowstone National Park. A recent study of understory plant species composition in Wyoming found higher cover of Ross's sedge in 30- to 50-year-old clearcut stands than in adjacent mature (>100 years) coniferous forest established after wildfire, supporting descriptions that it is an early to mid-seral species [88].

Ross's sedge is present on sites during the first 10 years following severe fire [97]. It has been described as common following stand-replacing fire in Wyoming lodgepole pine [69] and was found on Douglas-fir and subalpine fir habitat types in Yellowstone in the first 5 years after fire [6]. Its presence in early successional vegetation after fire is due to regeneration from surviving rhizomes and soil-stored seed [15,16,32,77,91,96]. For more information, see Fire Adaptations. Ross's sedge often dominates the forb layer of early-successional forest vegetation [57] and is found in open forest stands [39,62]. Though Ross's sedge may occasionally occur on forest sites with moderate to heavy shade, it is generally shade intolerant [54,57], becoming less important and eventually eliminated as it is overtopped by taller plants [57]. Ross's sedge forms a dry grassland association in clearcuts or burned areas of montane and subalpine coniferous forests in Colorado. These early-seral communities eventually give way to reestablished canopy species (e.g., limber pine, lodgepole pine). Shade from the closing canopy reduces Ross's sedge abundance. If the forest is slow to develop, however, Ross's sedge grasslands may persist for decades or centuries [79].

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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Taxonomy

provided by Fire Effects Information System Plants
The scientific name of Ross's sedge is Carex rossii Boott (Cyperaceae)
[23,29,30,33,36,40,41,43,45,47,49,51,52,53,74,84,93,109,110,111].
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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Value for rehabilitation of disturbed sites

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More info for the terms: reclamation, seed

Ross's sedge has been rated as "highly persistent" when used for reclamation. The extensive root system and ability to establish and persist on unstable as well as compacted soils make Ross's sedge an excellent soil builder with good erosion control capability [39]. Ross's sedge may establish from either transplants or seed. An Oregon study of campsite rehabilitation found that Ross's sedge had 100% transplant survival over 7 years, and transplants increased substantially in both height and area [21]. Following a road-building project, Ross's sedge dominated unseeded disturbed areas [64].

A greenhouse study found a greater number of Ross's sedge seedlings emerged from heated soil samples than from unheated soil samples [100].

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Anderson, Michelle D. 2008. Carex rossii. In: Fire Effects Information System, [Online]. 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/carros/all.html

Comprehensive Description

provided by North American Flora
Carex brevipes W. Boott, in S. Wats. Bot. Calif. 2: 246. 1880
Carex globosa var. W. Boott, in S. Wats. Bot. Calif. 2 : 485. 1880. (Based on C. brevipes W. Boott.) Carex deflexa var. Boottii L. H. Bailey, Mem. Torrey Club 1: 43. 1889. (Based on C. brevipes W.
Boott.) Carex Rossii var. brevipes Kiikenth. in Engler, Pflanzenreich 4™: 452. 1909. (Based on C brevipes
W. Boott.)
In dense clumps, from stout, matted, ascending rootstocks, without long horizontal stolons, the culms from very short to 18 cm. high, phyllopodic, reddish-purple-tinged and more or less strongly fibrillose at base, the longer exceeding the leaves, the shorter hidden at their base, erect, slender, triangular, roughened above; sterile culms conspicuous, elongate, aphyllopodic; leaves with well-developed blades 4-8 to a fertile culm, the blades thin but firm, green, channeled at base, flat above, with slightly revolute margins, up to 15 cm. long, 1.5-2.5 mm. wide, roughened towards apex, long-tapering; sheaths smooth dorsally, little or not at all breaking or filamentose ventrally, the ligule much wider than long; terminal spike staminate, slender, short-peduncled or sessile, 4-12 mm. long, 2.5 mm. wide, severalto many-flowered, the scales rather loose, oblong-obovate to ovate, acute to cuspidate, reddish-brown or lightpurplish-brown with lighter 3-nerved center and narrow hyaline margins; pistillate spikes 3-5, closely 6-20-flowered, the upper one or two approximate, erect, from sessile to strongly peduncled, the others widely separated, basal, long-peduncled, the perigynia in several rows, ascending; bract of lower non-basal spike leaflet-like, exceeding inflorescence, green, slightly purplish-auricled at base; scales ovate, acute to cuspidate, purplish-brown with broad 3nerved center and narrow hyaline margins, about width of but shorter than mature perigynia, exposing the upper part; perigynia small, 2.5 to nearly 3 mm. long, 1.25-1.5 mm. wide, green, puberulent, the body little longer than wide, suborbicular and obscurely triangular in crosssection, 2-keeled, otherwise nerveless, more or less strongly stipitate, abruptly contracted into a slender beak 0.25-0.75 mm. long, ciliate-serrulate, slightly colored or hyaline-tipped, shallowly bidentate; achenes triangular with strongly convex sides and conspicuous angles, closely enveloped, 1.5-2 mm. long, round-tapering and stipitate at base, truncate and shortapiculate at ape.x, jointed with the short, straight, slender style; stigmas three, slender.
Type locality: "In the Sierra Nevada; Lake Tahoe to Bear Valley, Kellogg." Distribution: From Washington southward in the mountains, especially in the Sierra Nevada, to southern California. (Specimens examined from California, Oregon, Washington.)
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Kenneth Kent Mackenzie. 1935. (POALES); CYPERACEAE; CARICEAE. North American flora. vol 18(4). New York Botanical Garden, New York, NY
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Comprehensive Description

provided by North American Flora
Carex rossii Boott, in Hook. Fl. Bor. Am. 2 : 222. 1839
Carex pennsylvanica var. (no. 2). Bock. Linnaea 41 : 220. 1877. (Based on C. Rossii Boott.) Carex Novae-Angliae var. Rossii L. H. Bailey, Bot. Gaz. 10: 207. 1885. (Based on C. Rossii Boott.) Carex Novae-Angliae var. deflexa L. H. Bailey, Proc. Am. Acad. 22: 124. 1886. (Type from westem United States.) Carex deflexa var. Rossii L. H. Bailey, Mem. Torrey Club 1 : 43. 1889. (Based on C. Rossii Boott.) Carex deflexa var. tnedia L. H. Bailey, Mem. Torrey Club. 1 : 43. 1889. (Based on C. Novae-Angliae
var. deflexa L. H. Bailey.) Not C. media R. Br. 1823. Carex deflexa var. Farwellii Britten; Britt. & Brown, 111. Fl. 1: 334. 1896. (Based on C. deflexa
var. media L. H. Bailey.) Carex Farwellii Mackenzie, Bull. Torrey Club 37: 244. 1910. (Based on C. deflexa var. Farwellii Britton.)
Clumps medium-sized, more or less densely cespitose, without long horizontal stolons, the rootstocks stout, lignescent, branching, ascending; culms 5-30 cm. high, slender but erect and strict, usually exceeding the leaves, triangular, slightly roughened above, strongly reddishpurple-tinged at base, the sterile shoots mostly conspicuous, elongate, aphyllopodic; fertile culms bearing several leaves with well-developed blades inserted towards the base, the blades ascending, usually less than 6 cm. long, 1-2.5 mm. wide, thin but firm, deep-green to light-green, slightly channeled above, the margins very slightly revolute, roughened on the margins and towards the apex, long-attenuate; leaves of sterile culms more numerous and with longer and somewhat wider blades; sheaths minutely hispidulous dorsally, little or not at all breaking or filamentose ventraUy, the ligule much wider than long; staminate spike sessile or short-peduncled, erect, 3-15 mm. long, 1-2.5 mm. wide, exceeding the contiguous pistillate spike, the scales oblong-obovate, closely appressed, obtuse to cuspidate, reddish-brown with 3ribbed green center and hyaline margins; pistillate spikes 3-5, the upper 1 or 2 erect, sessile or short-peduncled, approximate or somewhat separate, the lower widely separated, nearly basal, erect, on slender, often long peduncles, suborbicular or short-oblong, 3-5 mm. long, 3-4 mm. wide, closely flowered, the perigynia 3-15, ascending in few rows on the fiexuous rachis; lower bract leaflet-hke, normally exceeding culm, 0.5-5 cm. long, little if at all sheathing and hardly colored at base, the upper much shorter; scales ovate, acute to acuminate or cuspidate, or even awned, wider but shorter than the mature perigynia, greenish or reddish or purplish-brown, with 3-nerved green center and hyaline margins; perigynia 3-4.5 mm. long, short-pubescent, pale-green, membranaceous, the body 1.5-2.5 mm. long, 1 mm. wide, 2keeled but otherwise nerveless or nearly so, stipitate, tapering to a base 0.5-1.5 mm. long, abruptly contracted into a conic beak 0.75-1.5 mm. long, ciliate-serrulate, deeply bidentate; achenes obovoid-orbicular, very closely enveloped, obtusely triangular with convex sides and prominent angles, stipitate and tapering at base, truncate at apex and short-apiculate, jointed with the straight, slender style; stigmas three, slender.
TvPB UOCALiri': Northwest coast of N. America (.Douglas); Rocky Mountains (Drtimmond).
Distribution: Dry soil, mountains of Colorado to middle California, and northward to Yukon, eastward to the Black Hills of South Dakota, and locally to northern Michigan. (Specimens examined from Michigan, Minnesota, Manitoba, Saskatchewan, South Dakota, Alberta, Montana, Wyoming, Coloratlo, Utah, Idaho, British Columbia, including Vancouver Island, Yukon, Washington, Oregon, California.)
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Kenneth Kent Mackenzie. 1935. (POALES); CYPERACEAE; CARICEAE. North American flora. vol 18(4). New York Botanical Garden, New York, NY
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Carex rossii

provided by wikipedia EN

Carex rossii, commonly known as Ross's sedge, is a hardy species of sedge that is often a pioneer species in areas with little or no established vegetation, or in places where disturbance has occurred. Ross's sedge grows in a variety of habitats throughout much of western North America, from Alaska to Ontario, south to New Mexico and California. It flowers in May and June.[3][4][5]

Taxonomy

Carex rossii was first described by Francis Boott in Hooker's Flora Boreali-Americana (1839). The type locality was listed as "Hab. N. W. Coast. Douglas. Rocky Mountains. Drummond" (sic)".[6]

Description

Carex rossii produces a dense clump, or solid mat of slender stems up to about 40 centimetres (16 in) from a shallow network of rhizomes. The pale to dark green leaves are usually longer than the stems. The inflorescences contain one or more staminate flower spikes above more rounded pistillate spikes. The fruit is three-sided, and covered in a greenish or brownish perigynium.[3][4]

Distribution and habitat

Carex rossii is native to, and sometimes abundant in, Alaska and subarctic Canada (Nunavut, Northwest Territories, and Yukon Territory); western Canada (Alberta, British Columbia, Manitoba, and Saskatchewan); and the contiguous U.S. (Arizona, California, Colorado, the Dakotas, Idaho, Minnesota, Montana, Nevada, New Mexico, Oregon, Utah, Washington, and Wyoming.) It is found only sporadically in Ontario, Michigan, and Nebraska.[2][3][7]

It grows in many habitat types, including wet and dry areas in forest, sagebrush, prairie, and alpine meadows.[3][4][8]

References

  1. ^ "Name - Carex rossii Boott synonyms". Tropicos. Saint Louis, Missouri: Missouri Botanical Garden. Retrieved August 23, 2010.
  2. ^ a b "Profile for Carex rossii (Ross' sedge)". PLANTS Database. USDA, NRCS. Retrieved August 2, 2010.
  3. ^ a b c d Anderson, Michelle D. (2008). "Carex rossii". Fire Effects Information System (online). Rocky Mountain Research Station, Fire Sciences Laboratory (Producer): U.S.D.A; Forest Service. Retrieved August 23, 2010.
  4. ^ a b c Raymond Cranfill (1993). "Jepson Manual treatment for CAREX rossii". Jepson Manual Online. University & Jepson Herbaria; Regents of the University of California. Retrieved August 24, 2010.
  5. ^ Flora of North America: Carex rossii
  6. ^ "Plant Name Details for Carex rossii". IPNI. Retrieved August 23, 2010.
  7. ^ "Carex rossii". Germplasm Resources Information Network (GRIN). Agricultural Research Service (ARS), United States Department of Agriculture (USDA). Retrieved August 23, 2010.
  8. ^ Calflora: Carex rossii (Ross sedge)

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Carex rossii: Brief Summary

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Carex rossii, commonly known as Ross's sedge, is a hardy species of sedge that is often a pioneer species in areas with little or no established vegetation, or in places where disturbance has occurred. Ross's sedge grows in a variety of habitats throughout much of western North America, from Alaska to Ontario, south to New Mexico and California. It flowers in May and June.

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