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Bicknell's Cranesbill

Geranium bicknellii Britton

Broad-scale Impacts of Fire

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More info for the terms: forest, wildfire

Bicknell's cranesbill primarily occurs on burned lands. There are many documented instances where Bicknell's cranesbill was present after fire and not noted prior. Bicknell's cranesbill was present only after prescribed burning on black oak savannas at Hoosier Prairie Nature Preserve, Indiana [15], was found on burned land only in studies conducted after a variety of fires on jack pine sites in Superior National Forest, Minnesota [5], and was exclusive to jack pine sites burned under prescription and wildfire in northern lower Michigan [1,2]. The table below provides further evidence of Bicknell's cranesbill's absence from prefire communities.

Percent of plots (n=30) in which Bicknell's cranesbill was found in jack pine stands burned under prescription in northeastern Minnesota [6]

East Bearskin Lake

Grass Lake

Cut burned Cut unburned Cut burned Precut Postfire Precut Postcut Precut Postfire 1960 1961 1962 1963 1964 1960 1961 1963 1962 1963 1964 0 100 77 87 23 0 0 0 0 97 97
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Broad-scale Impacts of Plant Response to Fire

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More info for the terms: cover, duff, forest, frequency, litter, prescribed burn, prescribed fire, seed, series, severity, wildfire

Bicknell's cranesbill is abundant in early postfire communities and becomes infrequent or
absent in subsequent years [1,3,4,6,21,25,54,60,62,84,94]. Within 3 to 5 years after the
Sundance Fire in northern Idaho's western redcedar-western hemlock forest type,
Bicknell's cranesbill went from 50% frequency
to 0% and became absent at all study sites [74]. Bicknell's cranesbill cover
was 24% the first year following fire on jack pine sites in northern lower
Michigan and reduced to scattered individuals after 2 to 6 years [1,2]. After the Pattee
Canyon Fire burned through Douglas-fir habitat types in western Montana,
Bicknell's cranesbill bloomed and set seed in the first postfire year and almost
disappeared the second postfire year [25]. Sidhu [71] studied the early changes in biomass and frequency of
minor plant species following partial logging and prescribed burning in eastern white
pine forests near Chalk River, Ontario. Bicknell's cranesbill occurred in logged,
unburned stands with an average percent frequency of 5%. Its average percent frequency in
stands that were logged then burned was 23%. Sidhu states that Bicknell's cranesbill appeared, from seed origin, 3 weeks after burning and was predominant only after fire. Burning
was conducted in July and sampling in
August, 1972. Bicknell's cranesbill was not present before logging and burning. Sidhu [72]
continued sampling in September 1972 and June 1973 and provided average percent ground cover
data for Bicknell's cranesbill for all sample periods, as shown in the table below.
Bicknell's cranesbill cover on burned sites reached a maximum of 13% the summer
after treatment. This part of the series did not include data for Bicknell's cranesbill in the logged-unburned
stand, whereas, mentioned above, it was recorded previously.

Average percent ground cover of Bicknell's cranesbill at different times
following logging and prescribed burning in white pine forests of Ontario [72]

Treatment


Prefire (July 1972)
Time after fire
1 month (August 1972)
2 months (September 1972)
11 months (June 1973)
Stand
17
21
25
4
24
25
25
Logged-unburned
--
--
--
x
0.30
x
3.00
Logged-backfire
--
x
x
x
1.60
4.50
3.75
102B-headfire
--
x
x
0.20
6.00
6.95
13.10
x = Bicknell's cranesbill present
but with insignificant cover, -- = not present

Bicknell's cranesbill seedlings establish more densely with increasing fire
severity. Ohmann and Grigal [61]
contrasted vegetation responses following a spring burn (Little Sioux Fire) and
a summer burn (Prayer Lake Fire). The spring fire was low severity in jack
pine forest. It destroyed
the litter layer but left much of the cool, moist, lower soil layers intact. The
higher-severity summer fire consumed virtually all of the warm, dry forest
floor. Bicknell's cranesbill did occur following the Little Sioux Fire but was
much more abundant after the Prayer Lake Fire [61]. Average percent Bicknell's cranesbill frequency 4 years after the Black River fire in southeastern Manitoba
was 16% on scorched (litter not burned or partially burned), 44% on lightly
burned (litter burned but without or very limited duff consumption), and 59% on
severely burned (forest floor completely consumed) stands. The dominant
species were quaking aspen, balsam fir, white and black spruce, and/or jack
pine. Bicknell's cranesbill did not occur in a 10-year-old or mature stand
[88,89]. Study sites
on the Superior National Forest were subject to
prescribed fire and wildfire. An unburned portion was also included in the study
area. Bicknell's cranesbill occurred on burned lands only and was most prevalent
on the severely burned sites. Its percent frequency was 100% after high-severity
wildfire swept through jack pine-black spruce stands and 23% and 47%
in 2 stands of clearcut jack pine with some quaking aspen and paper birch after
a low-severity prescribed burn [5].

Hamilton's Research Paper
(Hamilton 2006b)
provides further information on prescribed fire and postfire response of species including Bicknell's cranesbill.
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Common Names

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Bicknell's cranesbill

Bicknell's geranium

northern cranesbill
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Conservation Status

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Information on state-level protected status of plants in the United States is available at Plants Database.
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Description

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More info for the term: forb

This description provides characteristics that may be relevant to fire ecology, and is not meant for identification. Keys for identification are available [9,33,36,42,49,57,67,78,86,90,91,92].

Bicknell's cranesbill is a native, annual or biennial forb. It has erect to decumbent stems ascending 4 to 24 inches (10-60 cm) [33,43,59] from a slender taproot [91]. In some cases Bicknell's cranesbill attains heights greater than 39 inches (100 cm) [9,86]. The flowers are few and small [73]. Fruits are cylindrical capsules and have long stiff hairs or bristles. Bicknell's cranesbill seeds are dark, oblong and finely pitted [43,47,59].

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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Distribution

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Bicknell's cranesbill occurs in Alaska and Yukon east to Newfoundland, south to Tennessee, Colorado, Utah, and California [9,33,43,45,67,91]. Bicknell's cranesbill is rare in South Dakota, Illinois, Indiana, Ohio, Pennsylvania, and Vermont. It is extirpated in Iowa and Connecticut [45]. Plants Database provides a distributional map of Bicknell's cranesbill.
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Fire Ecology

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More info for the terms: fire regime, fire-return interval, seed, stand-replacement fire, stand-replacing fire

Fire adaptations: Bicknell's cranesbill regenerates after fire from on-site seed stored in the soil seed bank [74,75,76,88,89].

FIRE REGIMES: Bicknell's cranesbill occurs in many fire-dependent ecosystems. FIRE REGIMES for plant communities with Bicknell's cranesbill vary from frequent understory fires in black oak, ponderosa pine, and larch and frequent stand-replacement fire in jack pine to infrequent, stand-replacement crown fires in white spruce. The northern boreal forests where Bicknell's cranesbill most often occurs are characterized by mixed-severity and stand-replacing FIRE REGIMES. Fire-return intervals in jack pine stands in eastern Canada and the Great Lakes were as low as 15 to 35 years. Fire-return intervals averaged between 50 and 150 years in white spruce stands [27].

The following table provides fire-return intervals for plant communities and ecosystems where Bicknell's cranesbill is important. 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".

Fire-return intervals for plant communities with Bicknell's cranesbill Community or Ecosystem Dominant Species Fire-Return Interval Range (years) sugar maple Acer saccharum >1,000 [87] tamarack Larix laricina 35-200 [63] western larch Larix occidentalis 25-350 [12,18,26] Great Lakes spruce-fir Picea-Abies spp. 35 to >200 northeastern spruce-fir Picea-Abies spp. 35-200 black spruce Picea mariana 35-200 conifer bog* Picea mariana-Larix laricina 35-200 [27] jack pine Pinus banksiana <35 to 200 [24,27] Rocky Mountain lodgepole pine* Pinus contorta var. latifolia 25-340 [17,18,80] Sierra lodgepole pine* Pinus contorta var. murrayana 35-200 Pacific ponderosa pine* Pinus ponderosa var. ponderosa 1-47 [11] interior ponderosa pine* Pinus ponderosa var. scopulorum 2-30 [11,16,50] red pine (Great Lakes region) Pinus resinosa 3-18 (x=3-10) [23,30] red-white pine* (Great Lakes region) Pinus resinosa-P. strobus 3-200 [24,40,52] eastern white pine Pinus strobus 35-200 [87] aspen-birch Populus tremuloides-Betula papyrifera 35-200 [27,87] quaking aspen (west of the Great Plains) Populus tremuloides 7-120 [11,37,56] Rocky Mountain Douglas-fir* Pseudotsuga menziesii var. glauca 25-100 [11,13,14] coastal Douglas-fir* Pseudotsuga menziesii var. menziesii 40-240 [11,58,66] black oak Quercus velutina <35 [87] western redcedar-western hemlock Thuja plicata-Tsuga heterophylla >200 [11] *fire-return interval varies widely; trends in variation are noted in the species review
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Fire Management Considerations

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More info for the term: low-severity fire

Since fire is required for germination of Bicknell's cranesbill's soil-stored seeds, the use of fire for management purposes could only have a positive effect on Bicknell's cranesbill populations. Severe fire would likely be more effective than low-severity fire for promoting Bicknell's cranesbill.
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Growth Form (according to Raunkiær Life-form classification)

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More info for the terms: hemicryptophyte, therophyte

RAUNKIAER [65] LIFE FORM:
Therophyte
Hemicryptophyte
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Habitat characteristics

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More info for the term: woodland

 Site descriptions for Bicknell's cranesbill State, Region, Province Site characteristics California Open woodlands, coniferous forests, and disturbed places; 2,000 to 4,900 feet (600-1,500 m) [42,59] Colorado 5,500 to 7,000 feet (1,700-2,100 m) [39] Illinois Sandy woods, fields; rare [57] Michigan Rock outcrops; clearings and burns, gravel pits, and trails in woods; open, usually dry, sandy or gravelly ground [86] Montana Open woods and clearings [20] Utah Shady moist roadsides at 6,000 to 8,000 feet (1,800-2400 m) [91] West Virginia Open woods and clearings [78] Alaska and adjacent Canada Woods, disturbed soil [44] Blue Ridge Open woods and clearings; infrequent [92] Great Plains Upland woods; rare [36] New England Roadsides, "waste land", dry ledges [69] Northeast US and adjacent Canada Open woods and fields [33] Pacific Northwest Woodland or open fields [43] Uinta Basin, Utah Burnt patches; 7,200 feet (2,200 m) [34] Nova Scotia Recently burned or cleared areas; rare [67]
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Habitat: Cover Types

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

More info for the term: cover

SAF COVER TYPES [29]:




1 Jack pine

5 Balsam fir

12 Black spruce

13 Black spruce-tamarack

15 Red pine

16 Aspen

18 Paper birch

21 Eastern white pine

27 Sugar maple

37 Northern white-cedar

38 Tamarack

53 White oak

107 White spruce

110 Black oak

201 White spruce

202 White spruce-paper birch

203 Balsam poplar

204 Black spruce

210 Interior Douglas-fir

212 Western larch

213 Grand fir

217 Aspen

218 Lodgepole pine

223 Sitka spruce

224 Western hemlock

225 Western hemlock-Sitka spruce

227 Western redcedar-western hemlock

228 Western redcedar

229 Pacific Douglas-fir

230 Douglas-fir-western hemlock

237 Interior ponderosa pine

244 Pacific ponderosa pine-Douglas-fir

245 Pacific ponderosa pine

251 White spruce-aspen

252 Paper birch

253 Black spruce-white spruce

254 Black spruce-paper birch
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Habitat: Ecosystem

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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):

ECOSYSTEMS [32]:




FRES10 White-red-jack pine

FRES11 Spruce-fir

FRES19 Aspen-birch

FRES20 Douglas-fir

FRES21 Ponderosa pine

FRES23 Fir-spruce

FRES24 Hemlock-Sitka spruce

FRES25 Larch

FRES26 Lodgepole pine
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Habitat: Plant Associations

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

More info for the terms: bog, forest

KUCHLER [48] PLANT ASSOCIATIONS:




K008 Lodgepole pine-subalpine forest


K011 Western ponderosa forest

K012 Douglas-fir forest

K014 Grand fir-Douglas-fir forest

K017 Black Hills pine forest

K018 Pine-Douglas-fir forest

K093 Great Lakes spruce-fir forest

K094 Conifer bog

K095 Great Lakes pine forest

K096 Northeastern spruce-fir forest

K107 Northern hardwoods-fir forest
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Habitat: Rangeland Cover Types

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

More info for the terms: cover, forest, shrubland

SRM (RANGELAND) COVER TYPES [70]:




109 Ponderosa pine shrubland

904 Black spruce-lichen

906 Broadleaf forest

920 White spruce-paper birch
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Immediate Effect of Fire

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More info for the term: top-kill

Bicknell's cranesbill is associated with early postfire environments [6,46] and is not usually recorded in stands prior to burning [1,2,5,6,15]. If it was present in the aboveground vegetation before fire, fire would likely top-kill Bicknell's cranesbill.
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Importance to Livestock and Wildlife

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More info for the term: cover

Deer preferred grazing Bicknell's cranesbill growing in young clearcut-and-burned sites in the Seeley-Swan area of northwestern Montana [54].

Palatability/nutritional value: No information is available on this topic.

Cover value: No information is available on this topic.

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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Key Plant Community Associations

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Bicknell's cranesbill is not a dominant species in any of the habitat types that
it occurs in. It most commonly occurs in northern boreal forests
consisting of varying amounts of jack pine (Pinus banksiana), eastern
white pine (P. strobus), red pine (P.
resinosa), white spruce (Picea glauca), black spruce (P. mariana),
balsam fir (Abies balsamea), quaking aspen (Populus
tremuloides), and paper birch (Betula
papyrifera) [7,31,38,55].
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bibliographic citation
Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Life Form

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More info for the term: forb

Forb
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Management considerations

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More info for the term: frequency

Bicknell's cranesbill was listed as a "weedy species" occurring (percent frequency
0.8%) on agricultural fields in Manitoba [82].
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Phenology

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Flowering dates for Bicknell's cranesbill State, Region, Province Anthesis period California July to August [59] Illinois June to August [57] West Virginia July to September [78] Blue Ridge July to September [92] Great Plains June to September [36] New England Late May to July [69] Northeast US and adjacent Canada May to September [33] Pacific Northwest May to August [43] Uinta Basin, Utah July [34] Nova Scotia Late June to July [67]
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Plant Response to Fire

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Bicknell's cranesbill responds favorably to fire and the conditions associated with the immediate postfire environment [6,46]. The passage of fire and accompanying high temperatures break dormancy of and stimulate the soil stored seeds to germinate [1,2,3,22,35,51,68,85,93]. Keown [46] states that as a general rule, the more "intense" a fire is, the more favorable the conditions are for Bicknell's cranesbill germination. Because Bicknell's cranesbill is a pioneer species with rapid growth, it most often establishes after fire. Plants die off without recurrent disturbance [10].
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Post-fire Regeneration

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More info for the term: ground residual colonizer

POSTFIRE REGENERATION STRATEGY [75]:
Ground residual colonizer (on-site, initial community)
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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Regeneration Processes

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More info for the terms: breeding system, cover, forest, root crown, seed, stratification, top-kill, wildfire

Bicknell's cranesbill regenerates from seed [5]. Information on pollination, breeding system, seed production, seed establishment, and growth are lacking for Bicknell's cranesbill. Research is needed on Bicknell's cranesbill regeneration.

Seed dispersal: The capsules of Bicknell's cranesbill open explosively, splitting lengthwise from the bottom and flinging seeds away from the parent plant [47]. The large seeds are not adapted for broad wind dispersal [31] but can be transferred by small mammals [5].

Seed banking: Bicknell's cranesbill stores long-lived propagules in the soil [10,74,75,76,77]. It germinates and flowers in the first 1 to 3 years after fire and stores seeds for long periods between brief postfire flowerings [41,60,68].

Bicknell's cranesbill seeds have been found in soils of stands 200+ years old; however, the viability of these seeds is unknown. A study conducted in the Boundary Waters Canoe Area, Minnesota, recovered seeds from soil samples taken from plots in which the time since last disturbance ranged from 3 to 200+ years. The plots occurred in stands of jack pine, red pine, eastern white pine, quaking aspen, balsam fir, paper birch, and white spruce. The viability of the seeds from the old growth was not revealed since seeds from all plots were combined to undergo germination tests. Thirty percent of the combined seeds germinated [7]. Fyles [31] reveals finding Bicknell's cranesbill seed in soil samples taken from mature jack pine and white spruce stands in central Alberta where parent plants did not occur. He suggests that the seed was deposited by plants growing in the stand in the past and that the population was maintained as a result of extended seed longevity [31].

Germination: The seeds of Bicknell's cranesbill, in most cases, are stimulated to germinate by fire-induced high temperatures [1,2,22,35,68,85,93]. Bicknell's cranesbill seeds present in both burned (Little Sioux wildfire) and unburned soils taken from 270-year-old red pine stands in the Boundary Waters Canoe Wilderness Area underwent greenhouse germination tests. Bicknell's cranesbill only germinated from soil taken from the burned land 3 years after fire, suggesting that heat is required to break dormancy [8]. A greenhouse study by Granstrom and Schimmel [35] revealed that dormancy was released after exposure to high temperatures (moist heat, water bath). There was progressively higher germination at temperatures above 100 to 110 °F (40-45 °C), with 90% germination after 10 minutes exposure at 150 to 210 °F (65-100 °C). Lethal temperatures for seeds were in the range of 200 to 230 °F (95-110 °C). Virtually no germination occurred in nonheated seeds [35].

Germination can also be triggered by the warming of the soil [47], such as when the canopy cover is removed. Bicknell's cranesbill was present on clearcuts on boreal mixed-wood (white spruce, black spruce, balsam fir, jack pine, quaking aspen, paper birch, balsam poplar) forests in Ontario, but was significantly (P<0.05) more abundant on wildfire sites dominated mainly by quaking aspen [38]. Bicknell's cranesbill was observed growing 3 and 5 years after clearcutting stands dominated by quaking aspen in Alberta. The harvested forest was of fire origin, but no further information on the fire was given [79].

Bicknell's cranesbill may germinate in the absence of heat treatments as well. Soil samples from partially cut or clearcut boreal stands in the Black Sturgeon Forest northeast of Thunder Bay, Ontario, underwent 3 months of cold storage to mimic stratification. Subsequent greenhouse germination tests were used to identify seed banking species. Bicknell's cranesbill did germinate from these soils; however, there was no mention of heat treatment applied to samples or recent fire on sampled sites. Bicknell's cranesbill was not found in the aboveground vegetation at the study site [64].

Vegetative regeneration: Information on vegetative regeneration in Bicknell's cranesbill is lacking. Bicknell's cranesbill may sprout from the root crown after top-kill; however, reproduction from seed is Bicknell's cranesbill's primary method of regeneration.

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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Regional Distribution in the Western United States

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

BLM PHYSIOGRAPHIC REGIONS [19]:




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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Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

States or Provinces

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(key to state/province abbreviations)
UNITED STATES AK CA CO CT ID IL IN IA ME MA MI MN MO MT NH NY ND OH OR PA RI SD TN UT VT VA WA WV WI WY
CANADA AB BC MB NB NF NT NS ON PQ SK YK
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bibliographic citation
Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Successional Status

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More info on this topic.

More info for the terms: climax, presence, seed

Bicknell's cranesbill is a shade intolerant, ephemeral, pioneer species that occurs after fire from soil stored seed [10,28,46,68,74] already present at the time of disturbance.

As a residual, colonizing species following fire [74], Bicknell's cranesbill most often occurs in early postfire communities; however, there is evidence that it can occur in later seral communities. Maycock [55] reports the presence of Bicknell's cranesbill in 75- to 85-year-old white spruce and balsam fir stands on the Keweenaw Peninsula, northern Michigan, that were free from "unnatural disturbance". The presence of charcoal in the soil indicated that the stand was of fire origin. Bicknell's cranesbill's presence was also recorded in a 130-year-old mixed stand dominated by sugar maple (Acer saccharinum) along with balsam fir, white spruce, and red pine [55]. There was no mention of previous fire in this stand. Taylor [81] reports the presence of Bicknell's cranesbill on open stream banks and meadows found within climax forests (mainly western hemlock-Sitka spruce (Picea sitchensis)) of southeastern Alaska.

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bibliographic citation
Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Synonyms

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More info for the term: fern

Geranium bicknellii Britt. var. longipes (Wats.) Fern. [59,90]

Geranium carolinianum L. var. longipes Wats. [39]
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bibliographic citation
Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Taxonomy

provided by Fire Effects Information System Plants
The scientific name of Bicknell's cranesbill is Geranium bicknellii
Britt. (Geraniaceae) [9,33,36,42,45,57,67,78,86,92].
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bibliographic citation
Reeves, Sonja L. 2007. Geranium bicknellii. 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/forb/gerbic/all.html

Comprehensive Description

provided by North American Flora
Geranium nemorale Suksd. Deuts. Bot. Monats. 16: 222. 1892
Annual or biennial. Stems usually simple at the base, erect or nearly so, 1-3 dm. long, retrorsely pubescent; leaf-blades thin, orbicular-reniform in outline and slightly angular, 2-5 cm. broad, the main divisions incised or cleft into ovate or oblong segments ; petioles and peduncles retrorsely pubescent ; pedicels delicately glandular-pubescent ; sepals awn-tipped, the outer ones 6-8 mm. long, the bodies elliptic or ovate-elliptic, pubescent like the pedicel, the tip slender; petals purple, slightly longer than the sepals; style-column 15-20 mm. long, minutely glandular-pubescent; carpel-bodies 3-3.5 mm. long, sparingly hirsute; seeds reticulate.
Type locality' : West Klickitat County, Washington.
Distribution : Washington.
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bibliographic citation
John Kunkel Small, Lenda Tracy Hanks, Nathaniel Lord Britton. 1907. GERANIALES, GERANIACEAE, OXALIDACEAE, LINACEAE, ERYTHROXYLACEAE. North American flora. vol 25(1). New York Botanical Garden, New York, NY
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Comprehensive Description

provided by North American Flora
Geranium bicknellii Britton, Bull. Torrey Club 24: 92. 1897
Geranium carolinianum longipes S. Wats. Bot. King's Expl. 50. 1871. Geranium longipes Goodding, Bot. Gaz. 37: 56. 1904.
Annual or biennial. Steins simple below and erect, or branched at the base, the branches more or less spreading, with loosed' spreading hairs; leaf-blades thickish, pentagonal in outline, or those of the lower leaves rather rounded, 2-7 cm. broad, the main divisions incised or cleft into oblong or lanceolate segments ; petioles, peduncles and pedicels glandular-pubescent; sepals awn-tipped, the outer ones 7.5-8.5 mm. long, the bodies lanceolate or oblong-lanceolate, rather villous, the tip slender, about one third as long as the bod}; petals rose-purple, about as long as the sepals ; style-column 16-22 mm. long, glandular-hirsute; carpel-bodies 3 mm. long, sparingly hirsute.
Type locality : Southeastern New York.
Distribution : Nova Scotia to British Columbia, New York, Montana, and Washington.
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bibliographic citation
John Kunkel Small, Lenda Tracy Hanks, Nathaniel Lord Britton. 1907. GERANIALES, GERANIACEAE, OXALIDACEAE, LINACEAE, ERYTHROXYLACEAE. North American flora. vol 25(1). New York Botanical Garden, New York, NY
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Geranium bicknellii

provided by wikipedia EN

Geranium bicknellii is a species of geranium known by the common names Bicknell's cranesbill and northern cranesbill. It is native to much of the northern half of North America, where it can be found in a number of forest and woodland habitats. This is an annual or biennial herb which grows hairy stems up to about half a meter long. It may be erect or lie near the ground. Each leaf is several centimeters long and wide and is divided into several lobes, each of which may have smaller lobes or teeth. Flowers grow singly or in pairs and have pointed sepals and small lavender petals, each with a notch in the tip. The fruit has a rounded body with a long, straight style about 2 centimeters in length and tipped with a small beak.

Geranium bicknellii is a fire-adapted species, occurring most abundantly in recently burned forests. The seeds remain dormant while buried in the forest floor, sometimes for centuries, until a fire removes the organic litter and exposes the seeds to sunlight. The geraniums will germinate, bloom, and set seed profusely for several years after the fire, until other plants grow large enough to shade them out. The new seeds will then lie dormant in the soil, waiting for the next fire.[1]

The leaves of this species and some related species are somewhat difficult to distinguish from those of some plants in the family Ranunculaceae, particularly members of the genera Aconitum and Delphinium. They have also been confused with members of the genus Ranunculus, which is also part of that family, such as the meadow buttercup, Ranunculus acris. As the species from this family with a similar leaf shape are toxic to ingest or sometimes even touch, especially in the case of Aconitum species, it is possible that this is an example of mimicry designed to reduce herbivory. However, it may simply be accidental, due to adaption to conditions. As the family Ranunculaceae is especially ancient, other families have had quite a lot of time to mimic their characteristics via selection by herbivory.[2][3]

References

  1. ^ Reeves, Sonja L. (2007). "Geranium bicknellii". Fire Effects Information System. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Retrieved September 23, 2011.
  2. ^ Ge, Sun (2011). "Fossil is best look yet at an ancestor of buttercups". A eudicot from the Early Cretaceous of China. Indiana University. Retrieved September 5, 2017.
  3. ^ Udurawane, Vasika (2011). "A Tale of Flowers and Seeds". The Evolution of Plants. Earth Archives. Retrieved September 5, 2015.

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Geranium bicknellii: Brief Summary

provided by wikipedia EN

Geranium bicknellii is a species of geranium known by the common names Bicknell's cranesbill and northern cranesbill. It is native to much of the northern half of North America, where it can be found in a number of forest and woodland habitats. This is an annual or biennial herb which grows hairy stems up to about half a meter long. It may be erect or lie near the ground. Each leaf is several centimeters long and wide and is divided into several lobes, each of which may have smaller lobes or teeth. Flowers grow singly or in pairs and have pointed sepals and small lavender petals, each with a notch in the tip. The fruit has a rounded body with a long, straight style about 2 centimeters in length and tipped with a small beak.

Geranium bicknellii is a fire-adapted species, occurring most abundantly in recently burned forests. The seeds remain dormant while buried in the forest floor, sometimes for centuries, until a fire removes the organic litter and exposes the seeds to sunlight. The geraniums will germinate, bloom, and set seed profusely for several years after the fire, until other plants grow large enough to shade them out. The new seeds will then lie dormant in the soil, waiting for the next fire.

The leaves of this species and some related species are somewhat difficult to distinguish from those of some plants in the family Ranunculaceae, particularly members of the genera Aconitum and Delphinium. They have also been confused with members of the genus Ranunculus, which is also part of that family, such as the meadow buttercup, Ranunculus acris. As the species from this family with a similar leaf shape are toxic to ingest or sometimes even touch, especially in the case of Aconitum species, it is possible that this is an example of mimicry designed to reduce herbivory. However, it may simply be accidental, due to adaption to conditions. As the family Ranunculaceae is especially ancient, other families have had quite a lot of time to mimic their characteristics via selection by herbivory.

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