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Creeping Bentgrass

Agrostis stolonifera L.

Associations

provided by BioImages, the virtual fieldguide, UK
In Great Britain and/or Ireland:
Foodplant / parasite
Blumeria graminis parasitises live Agrostis stolonifera

Plant / resting place / on
puparium of Cerodontha flavocingulata may be found on leaf of Agrostis stolonifera
Other: major host/prey

Foodplant / spot causer
immersed pseudothecium of Didymella hebridensis causes spots on dying leaf of Agrostis stolonifera
Remarks: season: 8

Foodplant / parasite
colony of Dreschler dematiaceous anamorph of Drechslera fugax parasitises live Agrostis stolonifera

Foodplant / gall
stroma of Epichlo causes gall of stem of Agrostis stolonifera
Remarks: season: fertile in 8

Foodplant / saprobe
Alternaria dematiaceous anamorph of Lewia infectoria is saprobic on dead, fungus infected Agrostis stolonifera

Foodplant / spot causer
colony of Mastigosporium anamorph of Mastigosporium rubricosum causes spots on live leaf of Agrostis stolonifera

Foodplant / pathogen
Meloidogyne minor infects and damages yellow patch of Agrostis stolonifera

Foodplant / pathogen
Fusarium anamorph of Monographella nivalis infects and damages leaf sheath (usually close to stem base) of Agrostis stolonifera
Remarks: season: mainly 10-3
Other: major host/prey

Foodplant / parasite
hypophyllous telium of Puccinia coronata parasitises live leaf of Agrostis stolonifera
Remarks: season: mid 8-

Foodplant / parasite
uredium of Puccinia graminis f.sp. agrostidis parasitises live stem of Agrostis stolonifera

Foodplant / parasite
hypophyllous, subepidermal telium of Puccinia recondita parasitises live leaf of Agrostis stolonifera

Foodplant / spot causer
immersed, thin, subcuticular stromatic plates of Rhynchosporium coelomycetous anamorph of Rhynchosporium orthosporum causes spots on live sheath of Agrostis stolonifera

Foodplant / pathogen
internal sorus of Tilletia sphaerococca infects and damages ovary of Agrostis stolonifera
Remarks: season: 9-10

Foodplant / saprobe
fruitbody of Typhula incarnata is saprobic on dying stem of Agrostis stolonifera

Foodplant / spot causer
long, linear, erumpent sorus of Urocystis agropyri causes spots on live, blistered leaf of Agrostis stolonifera

Foodplant / parasite
embedded sorus of Urocystis agrostidis parasitises live culm of Agrostis stolonifera

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Comments

provided by eFloras
An extremely variable species best recognised by the combination of stolons and a panicle which closes up after anthesis. Short rhizomes of up to 3 internodes are sometimes produced. It forms a close turf and is important in alpine pastures where it contributes significantly to the available fodder. 1500-4000 m.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of Pakistan Vol. 0: 480 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of Pakistan @ eFloras.org
editor
S. I. Ali & M. Qaiser
project
eFloras.org
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eFloras

Comments

provided by eFloras
This is a widespread and polymorphic species, adventive in many temperate countries.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 22: 340, 342, 343, 348 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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Description

provided by eFloras
Tufted, stoloniferous perennial forming a close turf; culms (5-)15-100 (-150) cm high, erect or geniculately ascending, smooth. Leaf-blades 1-10 cm long, 0.5-5 mm wide, flat, smooth or scaberulous; ligule 1.5-7 mm long, blunt. Panicle linear to lanceolate or oblong, 1-13(-30) cm long, open at anthesis, after-wards contracted and often dense, frequently lobed, the branches clustered, closely divided and spiculate in the lower part; inflated tip of pedicel scabrid. Spikelets 2-3 mm long, breaking up at maturity above the persistent glumes; glumes acute, awnless, rough on the keel; lemma 1.5-2.5 mm long, very blunt, usually awnless or with a short awn from near the tip; palea half to two-thirds the length of the lemma; anthers 1-1.5 mm long.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of Pakistan Vol. 0: 480 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of Pakistan @ eFloras.org
editor
S. I. Ali & M. Qaiser
project
eFloras.org
original
visit source
partner site
eFloras

Description

provided by eFloras
Perennial, tufted, stoloniferous; stolons slender, leafy, widely spreading, developing after anthesis. Culms erect or geniculate and rooting at base, 30–50(–100) cm tall. Leaf sheaths smooth; leaf blades linear, flat or inrolled, 4–10 cm × 2–5 mm, scaberulous, apex acute to acuminate; ligule on non-flowering shoots 2–3.5 mm, rounded to truncate, often lacerate. Panicle narrow, linear to lanceolate in outline, 5–20 cm, open only at anthesis, otherwise contracted, often dense; branches several per node, closely divided, ascending, scabrous, main branch at a node often bare in lower 1/3, but accompanied by shorter branches bearing spikelets to base. Spikelets 1.8–3 mm, yellowish green; glumes lanceolate, subequal or lower glume slightly longer, lower glume scabrous along keel distally, upper glume often smooth, apex acute; callus minutely hairy; lemma 3/4 as long to subequaling spikelet, usually awnless, apex rounded; palea 1/2–3/4 length of lemma. Anthers 0.8–1.5 mm. Fl. Aug.
license
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: 340, 342, 343, 348 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

Distribution

provided by eFloras
Distribution: Pakistan (Punjab, N.W.F.P., Gilgit & Kashmir); Europe, temperate Asia and North America; introduced in Australia, New Zealand, South America etc.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of Pakistan Vol. 0: 480 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of Pakistan @ eFloras.org
editor
S. I. Ali & M. Qaiser
project
eFloras.org
original
visit source
partner site
eFloras

Distribution

provided by eFloras
Europe, temperate Asia, N. America, elsewhere introduced.
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cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Annotated Checklist of the Flowering Plants of Nepal Vol. 0 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Annotated Checklist of the Flowering Plants of Nepal @ eFloras.org
author
K.K. Shrestha, J.R. Press and D.A. Sutton
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eFloras.org
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Elevation Range

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2400-3500 m
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Annotated Checklist of the Flowering Plants of Nepal Vol. 0 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Annotated Checklist of the Flowering Plants of Nepal @ eFloras.org
author
K.K. Shrestha, J.R. Press and D.A. Sutton
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eFloras.org
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Flower/Fruit

provided by eFloras
Fl. & Fr. Per. : July-August.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of Pakistan Vol. 0: 480 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of Pakistan @ eFloras.org
editor
S. I. Ali & M. Qaiser
project
eFloras.org
original
visit source
partner site
eFloras

Habitat & Distribution

provided by eFloras
Moist places along roadsides. Anhui, Gansu, Guizhou, Heilongjiang, Nei Mongol, Ningxia, Shaanxi, Shandong, Shanxi, Xinjiang, Xizang, Yunnan [Bhutan, India, Japan, Mongolia, Nepal, Russia; C and SW Asia, Europe].
license
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: 340, 342, 343, 348 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

Synonym

provided by eFloras
Agrostis palustris Hudson; A. sibirica V. A. Petrov.
license
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: 340, 342, 343, 348 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

Common Names

provided by Fire Effects Information System Plants
creeping bentgrass
redtop
carpet bentgrass
bentgrass
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Cover Value

provided by Fire Effects Information System Plants
Cover value of creeping bentgrass is rated good for upland game birds
and waterfowl and fair for small mammals and small nongame birds [24].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Description

provided by Fire Effects Information System Plants
Creeping bentgrass is a stoloniferous perennial, and is sometimes
mat-forming or tufted [19,21,22,23,44]. Culms are prostrate, usually
1.3 to 3.3 feet (0.4-1 m) long [19,21,26,41]. The blades are flat to
folded, 0.08-inch to 0.4-inch (2-10 mm) wide, and 0.8 to 4 inches (2-10
cm) long [23,26]. The panicle is open to somewhat narrow, and up to 16
inches (40 cm) tall [59].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Distribution

provided by Fire Effects Information System Plants
Creeping bentgrass is native to Eurasia and North Africa [59]. It was
probably introduced to North America prior to 1750, and has become
naturalized throughout the southern Canadian provinces and most of the
United States [34,59].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Fire Ecology

provided by Fire Effects Information System Plants
More info for the term: fire regime

Creeping bentgrass has fair tolerance to fire [62]. No information was
available in the literature concerning creeping bentgrass fire ecology
or adaptations. However, a similar species, ticklegrass (Agrostis
scabra), colonizes bare mineral soil on recently burned sites and may
store seeds in the soil for short durations, allowing for early
establishment of areas burned in the spring (see the FEIS write-up for
Agrostis scabra). The stolons are probably killed by moderately severe
and severe fires.

FIRE REGIMES :
Find 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".
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Fire Management Considerations

provided by Fire Effects Information System Plants
Since creeping bentgrass is considered an increaser species when
overgrazed, fire plans may have to be coordinated with grazing
management to ensure seedling establishment or inhibition.
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Growth Form (according to Raunkiær Life-form classification)

provided by Fire Effects Information System Plants
More info on this topic.

More info for the terms: geophyte, hemicryptophyte

Hemicryptophyte
Geophyte
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat characteristics

provided by Fire Effects Information System Plants
More info for the term: forest

Creeping bentgrass occurs in a wide variety of habitats including
woodlands, forest openings, grasslands, shrublands, prairies, sandhills,
meadows, marshes, bogs, vernal pools, and stream and lake margins
[7,9,30,35,36,59]. It is most commonly found in moist places such as
recently exposed sand and gravel bars, wet meadows, and along streams
[4,22,23,24,34]. Creeping bentgrass grows on disturbed sites such as
in ditches or along roadsides, and in pastures and hayfields
[19,23,44,58]. It also grows in salt marshes [7,61].

Creeping bentgrass grows best on moist to semiwet soils, but is
tolerant of poorly drained and subirrigated conditions, submergence,
and frequent flooding [4,24]. It grows best on loam, clay-loam, and
sandy soils, but occurs on gravelly and rocky substrates as well
[4,6,15,24]. It is moderately tolerant of drought [4].

Elevations for creeping bentgrass for several states and provinces are
as follows:

Montana 2,800-7,000 feet (854-2,134 m) [4,24]
Idaho 6,600-7,920 feet (2,000-2,400 m) [10]
Oregon 6,680 feet (2,036 m) [15]
Nevada 6,400-8,480 feet (1,950-2,585 m ) [36]
Utah 3,234-10,065 feet (980-3,050 m) [41]
California less than 3,300 feet ( less than 1000 m) [26]
Ontario 990 feet (300 m) [5]
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Cover Types

provided by Fire Effects Information System Plants
More info on this topic.

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

1 Jack pine
5 Balsam fir
12 Black spruce
15 Red pine
16 Aspen
17 Pin cherry
18 Paper birch
21 Eastern white pine
24 Hemlock - yellow birch
30 Red spruce - yellow birch
32 Red spruce
34 Red spruce - Fraser fir
39 Black ash - American elm - red maple
63 Cottonwood
95 Black willow
107 White spruce
108 Red maple
206 Engelmann spruce - subalpine fir
210 Interior Douglas-fir
217 Aspen
220 Rocky Mountain juniper
222 Black cottonwood - willow
233 Oregon white oak
235 Cottonwood - willow
237 Interior ponderosa pine
239 Pinyon - juniper
256 California mixed subalpine
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Ecosystem

provided by Fire Effects Information System Plants
More info on this topic.

This species is known to occur in the following ecosystem types (as named by the U.S. Forest Service in their Forest and Range Ecosystem [FRES] Type classification):

More info for the term: shrub

FRES10 White - red - jack pine
FRES11 Spruce - fir
FRES15 Oak - hickory
FRES17 Elm - ash - cottonwood
FRES19 Aspen - birch
FRES20 Douglas-fir
FRES21 Ponderosa pine
FRES23 Fir - spruce
FRES28 Western hardwoods
FRES29 Sagebrush
FRES30 Desert shrub
FRES34 Chaparral - mountain shrub
FRES35 Pinyon - juniper
FRES36 Mountain grasslands
FRES37 Mountain meadows
FRES38 Plains grasslands
FRES39 Prairie
FRES41 Wet grasslands
FRES44 Alpine
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Plant Associations

provided by Fire Effects Information System Plants
More info on this topic.

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

More info for the terms: bog, forest, shrub, woodland

K010 Ponderosa shrub forest
K011 Western ponderosa forest
K012 Douglas-fir forest
K016 Eastern ponderosa forest
K017 Black Hills pine forest
K018 Pine - Douglas-fir forest
K020 Spruce - fir - Douglas-fir forest
K021 Southwestern spruce - fir forest
K023 Juniper - pinyon woodland
K025 Alder - ash forest
K026 Oregon oakwoods
K031 Oak - juniper woodlands
K037 Mountain-mahogany - oak scrub
K038 Great Basin sagebrush
K040 Saltbush - greasewood
K047 Fescue - oatgrass
K049 Tule marshes
K050 Fescue - wheatgrass
K052 Alpine meadows and barren
K055 Sagebrush steppe
K064 Grama - needlegrass - wheatgrass
K066 Wheatgrass - needlegrass
K067 Wheatgrass - bluestem - needlegrass
K074 Bluestem prairie
K075 Nebraska Sandhills prairie
K093 Great Lakes spruce - fir forest
K094 Conifer bog
K095 Great Lakes pine forest
K096 Northeastern spruce - fir forest
K097 Southeastern spruce - fir forest
K098 Northern floodplain forest
K101 Elm - ash forest
K106 Northern hardwoods
K107 Northern hardwoods - fir forest
K108 Northern hardwoods - spruce forest
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Immediate Effect of Fire

provided by Fire Effects Information System Plants
Creeping bentgrass is probably top-killed by fire, as are most grasses.
Specific fire effects on creeping bentgrass are not described in the
literature.
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Importance to Livestock and Wildlife

provided by Fire Effects Information System Plants
Creeping bentgrass is important forage for livestock because it stays
green and palatable throughout the summer. In general, it is moderately
productive [23,24,59]. On moist sites, creeping bentgrass produces good
forage throughout the growing season, but is less productive and less
palatable than many introduced perennial grasses [59].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Key Plant Community Associations

provided by Fire Effects Information System Plants
More info for the terms: codominant, forest, grassland, herbaceous, marsh, shrubland

Creeping bentgrass occurs in a wide variety of habitats including
pinyon-juniper (Pinus-Juniperus spp.), aspen (Populus spp.), fir-spruce
(Abies-Picea spp.), ponderosa pine (P. ponderosa), willow (Salix spp.),
subalpine forest, meadow, and alpine [4,8,12,15,37]. It is an indicator
of riparian community types in the Intermountain region; willows are
usually the dominant overstory species [4,6,15,20].

Creeping bentgrass is a member of the semiarid shrubland community of
south-central Wyoming [6]. It is a member of the northern subarctic
community in Manitoba [53].

In West Newbury, Massachusetts, creeping bentgrass occurs in the
freshwater tidal marsh community on the Merrimack River [7].

Creeping bentgrass is a member of the herbaceous riparian plant
community on Santa Rosa Island, California. This community type is
interspersed with the grassland community type [9]. Creeping bentgrass
is a codominant species in a grass-sedge (Carex spp.) riparian area in
Idaho [10]. In Nebraska, creeping bentgrass occurs in a native lowland
prairie complex with wetland swales [11].

The following publication lists creeping bentgrass as a community
dominant:

Ecology and distribution of riparian vegetation in the Trout Creek
Mountains of southeastern Oregon [15]

Species not previously mentioned but commonly associated with creeping
bentgrass include true pinyon (Pinus edulis), Gambel oak (Quercus
gambelii), oneseed juniper (Juniperus monosperma), water birch (Betula
occidentalis), boxelder (Acer negundo), bigtooth maple (A.
grandidentatum), mountain maple (A. spicatum), hazel (Corylus cornuta),
cottonwood (Populus spp.), red-osier dogwood (Cornus sericea),
chokecherry (Prunus virginiana), Baltic rush (Juncus balticus), sedge,
Kentucky bluegrass (Poa pratense), fowl bluegrass (P. palustris),
Virginia strawberry (Fragaria virginiana), field horsetail (Equisetum
arvense), Canada thistle (Cirsium arvense), tufted hairgrass
(Deschampsia cespitosa), timothy (Phleum pratense), red clover
(Trifolium pratense), white clover (T. repens), broadleaf plantain
(Plantago major), saltgrass (Distichlis spicata), western aster (Aster
occidentalis), Rocky Mountain iris (Iris missouriensis), longleaf phlox
(Phlox longifolia), bush cinquefoil (Potentilla fruticosa), Wood's rose
(Rosa woodsii), bearberry honeysuckle (Lonicera involucrata), and
western yarrow (Achillea millefolium) [6,9,10,13,22].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Life Form

provided by Fire Effects Information System Plants
More info for the term: graminoid

Graminoid
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Management considerations

provided by Fire Effects Information System Plants
More info for the term: stolon

Overgrazing on sites formerly dominated by native grasses produces
changes in vegetational communities. Once a suitable site is disturbed,
the extensive stolon system of creeping bentgrass allows it to rapidly
spread and establish. It also withstands high levels of grazing, making
replacement with former dominants difficult [24].

Creeping bentgrass is tolerant of close grazing due to its somewhat
prostrate growth form, rhizomatous growth habit, and lower palatability
than associated species. If creeping bentgrass is used as a pasture
grass, close grazing followed by rest in a rotation system is
recommended to keep plants producing palatable forage all season.
Plants should be cut during early flowering to obtain highest quality
hay [23,24].

Creeping bentgrass readily colonizes areas disturbed by logging,
plowing, burning, or excessive grazing [23,56].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Nutritional Value

provided by Fire Effects Information System Plants
Creeping bentgrass is rated good in nutritional value for elk and mule
deer, poor for pronghorn, and fair for white-tailed deer, small mammals,
small nongame birds, upland game birds, and waterfowl [4,24]. Energy
rating is fair and protein content is poor [24].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Occurrence in North America

provided by Fire Effects Information System Plants
AL AK AZ CA CO CT DE GA HI ID
KY ME MD MA MI MN MO MT NE NV
NH NJ NM NY NC ND OH OR PA RI
SC SD TN TX UT VT VA WA WV WI
WY AB BC MB NF ON PQ SK
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Other uses and values

provided by Fire Effects Information System Plants
Creeping bentgrass is widely used in turf culture, especially for golf
courses [59].
license
cc-publicdomain
bibliographic citation
Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Palatability

provided by Fire Effects Information System Plants
Creeping bentgrass has a high palatability rating in the spring and
early summer, fair after flowering, and poor in winter [4,24]. It is
rated fair to good for livestock and highly satisfactory for elk
[23,24].
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Phenology

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More info on this topic.

Creeping bentgrass flowers from June to August in the Upper Great Plains
[21]. It flowers from June to October in the Carolinas [44].
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Plant Response to Fire

provided by Fire Effects Information System Plants
More info for the terms: mesic, restoration, swale, woodland

In 1972, prescription burning at the Buffalo River State Park in
northwest New Mexico was initiated as a tallgrass prairie management and
restoration technique. The response of creeping bentgrass to burning
varied with the site. On a nearly level mesic site in a badly disturbed
prairie, stimulation of flowering occurred at postfire year 1.
Inhibition of flowering occurred, however, on a wet swale site in an
undisturbed prairie [42].

In 1950, a fire burned 1,000,000 acres (400,000 ha) of woodland in
Alberta and British Columbia. Creeping bentgrass established on plots
where seeded species did not produce full stands [2].
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Post-fire Regeneration

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More info for the terms: graminoid, secondary colonizer

Tussock graminoid
Initial-offsite colonizer (off-site, initial community)
Secondary colonizer - on-site seed
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Regeneration Processes

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More info for the term: seed

Creeping bentgrass reproduces by seed and by stolons [14,53]. It can
set seed in one growing season, thus sometimes functioning as an annual.
In southern Ontario, creeping bentgrass seed has a 52 percent
germination rate after 30 days under approximate optimal germination
conditions; seeds were cold stratified for 9 months prior to planting
[53]. Grasses in the genus Agrostis are seed-banking species [60]. In
pastures and meadows of Europe, creeping bentgrass seeds can survive in
the soil for at least 1 year [48]. In a northern subarctic community in
Manitoba, Canada, creeping bentgrass is a persistent perennial that
spreads vegetatively to form clumps or large patches but sometimes fails
to reproduce by seed, although flowering is observed [53].
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Regional Distribution in the Western United States

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More info on this topic.

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):

1 Northern Pacific Border
2 Cascade Mountains
3 Southern Pacific Border
4 Sierra Mountains
5 Columbia Plateau
6 Upper Basin and Range
7 Lower Basin and Range
8 Northern Rocky Mountains
9 Middle Rocky Mountains
10 Wyoming Basin
11 Southern Rocky Mountains
12 Colorado Plateau
13 Rocky Mountain Piedmont
14 Great Plains
15 Black Hills Uplift
16 Upper Missouri Basin and Broken Lands
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Successional Status

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More info on this topic.

More info for the term: facultative wetland species

Facultative Seral Species

Creeping bentgrass is generally a pioneer or invader species [4,15,36],
but is tolerant of semishaded environments [62]. It is a facultative
wetland species in Montana and California [36,46]. It is a member of
the creeping bentgrass community type in riparian areas of Montana that
will eventually be taken over by later successional species [4,24].
Creeping bentgrass may persist under a regime of repeated fluvial
disturbance in wetland riparian areas of Montana [25]. In Oregon,
creeping bentgrass is an early successional species that colonizes
low-lying gravel bars and newly formed depositional surfaces [15]. In
Nevada, it is an increaser on moist sites; the creeping bentgrass
community type probably resulted because of past heavy grazing levels.
It may have replaced communities dominated by tufted hairgrass [36].
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Synonyms

provided by Fire Effects Information System Plants
Agrostis alba var. stolonifera
A. palustris
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Taxonomy

provided by Fire Effects Information System Plants
The currently accepted scientific name of creeping bentgrass is Agrostis
stolonifera L. [22,23,59]. It is a member of the Poaceae family.
Recognized varieties are [7,21,22,26,57]:

A. s. var. compacta Hartm.
A. s. var. palustris (Huds.)Farw.
A. s. var. stolonifera

Creeping bentgrass hybridizes with rabbitfoot grass (Polypogon
monspeliensis) and colonial bentgrass (A. capillaris). It apparently
hybridizes with ticklegrass (A. scabra), spike bentgrass (A. exarata)
and water polypogon (P. semiverticillatus) [59].

The names A. gigantea, A. alba, and A. stolonifera var. major have been
misapplied to creeping bentgrass, which is recognized as distinct from
those species [21,26].
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Value for rehabilitation of disturbed sites

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More info for the term: mesic

Creeping bentgrass is moderately effective in stabilizing streambanks
due to its typically dense network of intertwining roots and rhizomes.
However, bank undercutting and sloughing may occur, especially when
soils are wet or stands are weakened by excessive grazing [4,24].
Erosion control, short-term revegetation potential, and long-term
revegetation potential are rated high for creeping bentgrass [24]. In
subalpine and spruce-fir (Picea-Abies) habitats of the Intermountain
West, creeping bentgrass is recommended for direct seeding and
transplanting on riparian sites. Transplant capability is good, growth
rate is moderate, and flooding tolerance is moderate [43]. Creeping
bentgrass is used in the Northeast for erosion control [50].

An abandoned tailings pond from a zinc-lead mill near Pecos, New Mexico,
was sampled after 50 years of mining. An ephemeral stream ran through
the tailings pond and had resulted in extensive flooding and deposition
of sediment on top of original tailings. A distinct vegetational
community had developed and creeping bentgrass was found in the mesic
meadow site. High levels of zinc and lead were found in vegetation
being grazed by cattle.
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Esser, Lora L. 1994. Agrostis stolonifera. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Comprehensive Description

provided by North American Flora
Agrostis stolonifera L. Sp. PI. 62. 1753
Decandolia stolonifera Bastard, Fl. Maine-et -Loire 29. 1809. (Based on Agrostis stolonifera L.) Vilfa stolonifera Beauv. Agrost. 16, 148, 182. 1812. (Based on Agrostis stolonifera L.) Agrostis alba var. stolonifera Smith, Engl. Fl. 1: 93. 1824. (Based on A. stolonifera L.) Agrostis vulgaris var. stolonifera Koch, Syn. Fl. Germ. 782. 1837. (Based on A. stolonifera L.)
Perennial; culms ascending from a spreading base, the decumbent portion rooting in wet soil, mostly 2or 3-noded, 20-50 cm. tall; sheaths glabrous; ligule as much as 6 mm. long on the culm-leaves, on the innovations 2-3 mm. long; blades scabrous, usually rather numerous, 5-15 cm. long, 1-3 mm. wide; panicle oblong, pale or purple, somewhat open, 5-15 cm. long, the branches, or some of them, spikelet-bearing from near the base, ascending or spreading, the longer 3-5 cm. long, scabrous, naked below; spikelets 2-3 mm. long; glumes acute, glabrous, the first scabrous on the keel ; lemma shorter than the glumes, awnless or rarely awned from the back; palea half to two thirds as long as the lemma.
T >e locality: Europe.
Distribution: Moist grassy places, Newfoundland to Alaska, and southward to New Jersey in the East and Oregon in the West; also in northern Eurasia.
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Albert Spear Hitchcock. 1937. (POALES); POACEAE (pars). North American flora. vol 17(7). New York Botanical Garden, New York, NY
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Comprehensive Description

provided by North American Flora
Agrostis palustris Huds. Fl. Angl. 27. 1762
Agrostis polymorpha var. palustris Huds. Fl. Angl. ed. 2. 32. 1778. (Based on A. palustris Huds.)
Agrostis maritima Lam. Encyc. 1: 61. 1783. (Type from France.)
Agrostis alba var. palustris Pers. Syn. PI. 1: 76. 1805. (Based on A. palustris Huds.)
Milium maritimum Clem. Ensayo Var. Vid 285. 1807. (Based on Agrostis maritima Lam.)
Agrostis decumbens Gaudin; Muhl. Descr. Gram. 68. 1817. Not A. decumbens Host, 1809. (Type
from Pennsylvania.) Vilfa stolonifera var. maritima S. F. Gray, Nat. Arr. Brit. PI. 2: 146. 1821. (Based on Agrostis
maritima "With." [error for Lam.].) Apera palustris S. F. Gray, Nat. Arr. Brit. PI. 2: 148. 1821. (Based on Agrostis palustris "With."
[error for Huds.].) Agrostis alba var. maritima G. Meyer, Hannov. Mag. 1823: 138. 1824. (Based on .4. maritima
Lam.) Agrostis stolonifera var. maritima Koch, Syn. Fl. Germ. 781. 1837. (Based on A. maritima Lam.) ? Agrostis alba var. decumbens Eaton & Wright, N. Am. Bot. 117. 1840. (Not definitely based on
A. decumbens Gaudin.) Agrostis depressa Vasey, Bull. Torrey Club 13: 54. 1886. (Type from Clear Creek Canyon, Colorado, Patterson in 1885.) Agrostis exarala var. stolonifera Vasey, Bull. Torrey Club 13: 54. 1886. (Type from Columbia
River, Suksdorf.) Agrostis reptans Rydb. Fl. Rocky Mts. 54. 1917. (Based on A. exarala var. stolonifera Vasey.) Agrostis stolonifera var. palustris Farwell, Rep. Mich. Acad. 21: 351. 1920. (Based on A. polymorpha var. palustris Huds.)
Perennial, with long stolons; culms usually decumbent and rooting at base; blades narrower, more appressed, and stiffer than in A . stolonifera; panicle narrow, condensed or sometimes somewhat open; otherwise as in A. stolonifera. Type locality: England.
Distribution: Marshes along the coast from Newfoundland to Maryland; British Columbia
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Albert Spear Hitchcock. 1937. (POALES); POACEAE (pars). North American flora. vol 17(7). New York Botanical Garden, New York, NY
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Physical Description

provided by USDA PLANTS text
Perennials, Terrestrial, not aquatic, Stolons or runners present, Stems nodes swollen or brittle, Stems erect or ascending, Stems geniculate, decumbent, or lax, sometimes rooting at nodes, Stems caespitose, tufted, or clustered, Stems terete, round in cross section, or polygonal, Stem internodes hollow, Stems with inflorescence less than 1 m tall, Stems, culms, or scapes exceeding basal leaves, Leaves mostly basal, below middle of stem, Leaves conspicuously 2-ranked, distichous, Leaves sheathing at base, Leaf sheath mostly open, or loose, Leaf sheath smooth, glabrous, Leaf sheath and blade differentiated, Leaf blades linear, Leaf blades very narrow or filiform, less than 2 mm wide, Leaf blades 2-10 mm wide, Leaf blades mostly flat, Leaf blade margins folded, involute, or conduplicate, L eaf blades mostly glabrous, Ligule present, Ligule an unfringed eciliate membrane, Inflorescence terminal, Inflorescence an open panicle, openly paniculate, branches spreading, Inflorescence a contracted panicle, narrowly paniculate, branches appressed or ascending, Inflorescence solitary, with 1 spike, fascicle, glomerule, head, or cluster per stem or culm, Inflorescence branches more than 10 to numerous, Lower panicle branches whorled, Flowers bisexual, Spikelets laterally compressed, Spikelet less than 3 mm wide, Spikelets with 1 fertile floret, Spikelets solitary at rachis nodes, Spikelets all alike and fertille, Spikelets bisexual, Spikelets disarticulating above the glumes, glumes persistent, Spikelets disarticulating beneath or between the florets, Rachilla or pedicel glabrous, Glumes present, empty bracts, Glumes 2 clearly present, Glumes equal or subequal, Glumes equal to or longer than adjacent lemma, Glume equal to or longer than spikelet, Glumes 1 nerved, Lemmas thin, chartaceous, hyaline, cartilaginous, or membranous, Lemma 5-7 nerved, Lemma glabrous, Lemma apex truncate, rounded, or obtuse, Lemma awnless, Lemma margins thin, lying flat, Lemma straight, Palea present, well developed, Palea membranous, hyaline, Palea shorter than lemma, Palea 2 nerved or 2 keeled, Stamens 3, Styles 2-fid, deeply 2-branched, Stigmas 2, Fruit - caryopsis, Caryopsis ellipsoid, longitudinally grooved, hilum long-linear.
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Agrostis stolonifera

provided by wikipedia EN

Agrostis stolonifera (creeping bentgrass, creeping bent, fiorin, spreading bent or carpet bentgrass[2][3][4]) is a perennial grass species in the family Poaceae.

Description

Agrostis stolonifera is stoloniferous and may form mats or tufts. The prostrate stems of this species grow to 0.4–1.0 metre (1 ft 4 in – 3 ft 3 in) long with 2–10-centimetre (0.79–3.94 in) long leaf blades and a panicle reaching up to 40 cm (16 in) in height.

The ligule is pointed and up to 5 millimetres (0.20 in) long. This differs from common bent, Agrostis capillaris, which is short and does not come to a point.

The leaves are tapering, often with a blue-grey colour. The grass is not tufted and the spikelets are red and tightly closed within the panicle.[5] It flowers in July and August.

ligule is pointed up to 5mm long
leaf blade

Distribution

It can be found growing in a variety of habitats including woodlands, grasslands and meadows, wetlands, riparian zones, and as a pioneer species on disturbed sites.[4] It is native to Eurasia and North Africa (Algeria, Morocco and Tunisia). It is possible that it may also be native to northern parts of North America, and in any case it has been widely introduced and naturalised on that continent and in many other places.[3]

It is a constituent of wet habitats such as marshy grasslands. Some of its species have adapted to contaminated conditions and can cope with heavy metals. It can exist up to 2,500 feet (760 m).[6]

Cultivation

It is the most commonly used species of Agrostis.[7]

It is used for turf in gardens and landscapes, particularly on golf courses.[4] Many of the putting greens as well as an increasing number of fairways in the northern USA are creeping bentgrass.

Transgenic Varieties

In the 1990s, Scotts Miracle-Gro and Monsanto led early work in creeping bentgrass transgenics looked at glyphosate-resistance. However, due to easy wind pollination, seeds were accidentally dispersed from an experimental farm in Oregon in 2003. Scotts Miracle-Gro was fined $500,000 as a result.[8] In 2017, the USDA agreed not to regulate it at Scotts request, which meant that Scotts "will no longer be legally required to pay to clean up the grass after 2017, though it has promised to do so."[9] A 2004 gene flow study (with scientific sampling methods) documents gene flow on a landscape level, with a maximum at 21 kilometres (13 mi) and 14 km (8.7 mi) (respectively) in sentinel and resident plants observed by scientist, located in primarily nonagronomic places such as irrigation ditches.[10]

Other work in transgenic bentgrass looks into salinity tolerance. The improved performance of the transgenic plants was associated with higher relative water content, higher sodium uptake and lower solute leakage in leaf tissues, with higher concentrations of Na+, K+, Cl- and total phosphorus in root tissues, and with higher auxin accumulation rate in the root tissue. This transgenic plant can survive in the presence of 1.7% sodium chloride (half seawater salinity concentration), while the non transgenic line and wild type plants cannot.[11]

References

  1. ^ Lansdown, R.V. (2014). "Agrostis stolonifera". IUCN Red List of Threatened Species. 2014: e.T164020A42383133. doi:10.2305/IUCN.UK.2014-1.RLTS.T164020A42383133.en. Retrieved 19 November 2021.
  2. ^ a b USDA, NRCS (n.d.). "Agrostis stolonifera". The PLANTS Database (plants.usda.gov). Greensboro, North Carolina: National Plant Data Team. Retrieved 2010-03-16.
  3. ^ a b "Agrostis stolonifera". Germplasm Resources Information Network (GRIN). Agricultural Research Service (ARS), United States Department of Agriculture (USDA). Retrieved 2010-03-16.
  4. ^ a b c Esser, Lora L. (1994). "Agrostis stolonifera". Fire Effects Information System (FEIS). US Department of Agriculture (USDA), Forest Service (USFS), Rocky Mountain Research Station, Fire Sciences Laboratory. Retrieved 2010-03-16.
  5. ^ BSBI Description Archived 2011-07-17 at the Wayback Machine retrieved 2010-11-16.
  6. ^ C. E. Hubbard (1978). Grasses. Penguin Books. ISBN 9780140132274.
  7. ^ L. Watson; M. J. Dallwitz (2008). "The grass genera of the world: descriptions, illustrations, identification, and information retrieval; including synonyms, morphology, anatomy, physiology, phytochemistry, cytology, classification, pathogens, world and local distribution, and references". The Grass Genera of the World. Archived from the original on 2008-07-24. Retrieved 2009-08-19.
  8. ^ Notarianni, John (July 21, 2018). "How A Botched Experiment Sent GMO Grass Creeping Across Oregon". OPB. Retrieved 29 November 2022.
  9. ^ Main, Douglas (January 17, 2017). "USDA Agrees to Not Regulate Genetically Modified Grass On the Loose In Oregon". Retrieved 29 November 2022.
  10. ^ Lidia S. Watrud; E. Henry Lee; Anne Fairbrother; Connie Burdick; Jay R. Reichman; Mike Bollman; Marjorie Storm; George King & Peter K. Van de Water (2004). "Evidence for landscape-level, pollen-mediated gene flow from genetically modified creeping bentgrass with CP4 EPSPS as a marker". Proceedings of the National Academy of Sciences. 101 (40): 14533–14538. Bibcode:2004PNAS..10114533W. doi:10.1073/pnas.0405154101. PMC 521937. PMID 15448206.
  11. ^ ZHIGANG LI, Christian M. Baldwin, Qian Hu, Haibo Liu, Hong Luo (2010). Heterologous Expression of Arabidopsis H+-PPase Enhances Salt Tolerance in Transgenic Creeping Bentgrass (Agrostis stolonifera L.). Plant, Cell and Environ, Volume 33 Issue 2, P. 272–289.
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Agrostis stolonifera: Brief Summary

provided by wikipedia EN

Agrostis stolonifera (creeping bentgrass, creeping bent, fiorin, spreading bent or carpet bentgrass) is a perennial grass species in the family Poaceae.

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