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Tall Bluebells

Mertensia paniculata (Ait.) G. Don

Broad-scale Impacts of Plant Response to Fire

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

Underground vegetative parts allow for tall bluebells regeneration after
fire. Mann and Plug [47] excavated 5 tall
bluebells individuals and found plants were spreading laterally by adventitious
roots, some as deep as 2 inches (5 cm) below the mineral soil surface. On this
basis they inferred that tall bluebells can reproduce after fires by sprouting.
Vegetative regeneration of tall bluebells following the 1999 Black River
wildfire on quaking aspen boreal forests in southeastern Manitoba was recorded
for each fire severity class. During the 1st 4 years after fire, tall bluebells
was least abundant on severely burned plots [72,73].

Fire severity


Mean percent cover
Mean percent frequency
Scorched (litter not burned or partially burned) 1.1 11
Lightly burned (litter burned but without or with very
limited duff consumption) 2.9 23
Severely burned (forest floor completely consumed) <0.1 1

Tall bluebells responds favorably after fire. It established on mesic sites
in the 2nd growing season following a prescribed fire on a jack pine clearcut in
Saskatchewan [13]. Tall bluebells was present on 6 of 21 burned stands 12 to 15
years following fire on boreal forests in southeastern Manitoba. Mean percent
tall bluebells cover was 0.9% [38]. Frequency and cover of tall bluebells were
not significantly affected by a prescribed burn on Lutz spruce (Picea × lutzii) stands in Alaska. Tall
bluebells cover before and 7 years after fire was 8% to 6%, respectively, and frequency ranged
from 12% before to 18% seven years after fire. Tall bluebells cover and frequency
on unburned transects increased in the same years. Cover went from 2%
before fire to 8% after fire, and frequency from 15% to 31% [33]. Whether regeneration came from
off-site seed or vegetative sprouting was not indicated in either article.

Studies on tall bluebells regeneration from seed after fire are few and
inconclusive. Soil block samples collected a week after wildfire on a
quaking aspen boreal forest in Alberta were observed under greenhouse conditions to determine the
effects of burn severity on seed banks, vegetative banks, and emergent understory
species 2 years following fire. Tall bluebells did not germinate in soil samples
and had a very low vegetative bank index (proportion of rhizomes present among all blocks;
n=30) of 0.03 on blocks taken from
"intensely" (complete consumption of
aboveground vegetation) burned and unburned sites. Mean
percent cover for tall bluebells as an emergent understory species 2 years
following fire was: 5.65% on intensely burned sites, 4.28% on "lightly"
(characterized by death of aboveground plant parts) burned sites, and 1.19% on
unburned sites [43]. In 1972, a study site on quaking aspen stands in central
Alberta was burned under prescription. The site was reburned in 1978. Tall bluebells was
not observed on either control or burned plots after the 1972 fire. It was, however, found
on reburned plots in 1978 [55]. It is possible that in these studies, tall bluebells emerged on the burned areas
from an off-site seed source. See the Research Project Summary
Understory recovery after burning and reburning quaking aspen stands in central Alberta

for an extended report on the Quintilio and others [55] study.
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Common Names

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Species name―

tall bluebells

tall mertensia

panicled bluebells

lungwort



Infrataxa―

Alaska tall bluebells

northern bluebells

Eastwood's bluebells
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/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. 2006. Mertensia paniculata. 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/merpan/all.html

Distribution

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Tall bluebells is native to North America. It is distributed from Alaska east to Quebec and south to Wisconsin and Oregon. Disjunct populations of tall bluebells occur in Connecticut [1,26,37,70].

Distribution of varieties: Of the tall bluebells varieties, the typical variety is the most widespread. Its distribution is identical to that of the species. Alaska tall bluebells is limited to Alaska, Yukon, and Northwest Territory [37]. Northern bluebells occurs in northwestern Montana, adjacent Idaho, and British Columbia south to Washington and Oregon [30,37]. Eastwood's bluebells is present in Alaska and Northwest Territory [1,37]. Plants Database provides a distributional map of tall bluebells and its varieties.

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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Fire Ecology

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More info for the terms: fire regime, forest, mixed-severity fire, mixed-severity fire regime, seed

Fire adaptations: Postfire regeneration for tall bluebells is mostly vegetative. Tall bluebells sprouts from surface or buried vegetative parts [72]. Buried rhizomes are most likely to sprout. Tall bluebells may also regenerate from off-site seed sources after fire. Neither seed dispersal nor seedling establishment is documented for tall bluebells, with or without fire. Further research is needed on tall bluebells's fire ecology.

FIRE REGIMES: The white-black spruce boreal forest ecosystems where tall bluebells most commonly occurs are susceptible to frequent (35-200 years), stand-replacing fires because of the accumulation of large amounts of highly flammable organic matter. Tall bluebells is also common in quaking aspen-dominated boreal forest ecosystems that are characteristic of a mixed-severity fire regime [20].

The following table provides fire return intervals for plant communities and ecosystems where tall bluebells is important. For further information, see the FEIS review of the dominant species listed below.

Community or Ecosystem Dominant Species Fire Return Interval Range (years) grand fir Abies grandis 35-200 [3] birch Betula spp. 80-230 [65] tamarack Larix laricina 35-200 [53] Great Lakes spruce-fir Picea-Abies spp. 35 to >200 [20] Engelmann spruce-subalpine fir Picea engelmannii-Abies lasiocarpa 35 to >200 [3] black spruce P. mariana 35-200 conifer bog* P. mariana-Larix laricina 35-200 [20] jack pine Pinus banksiana <35 to 200 [14,20] Rocky Mountain lodgepole pine* P. contorta var. latifolia 25-340 [6,7,66] Sierra lodgepole pine* P. contorta var. murrayana 35-200 western white pine* P. monticola 50-200 [3] aspen-birch Populus tremuloides-Betula 35-200 [20,71] quaking aspen (west of the Great Plains) P. tremuloides 7-120 [3,27,49] Rocky Mountain Douglas-fir* Pseudotsuga menziesii var. glauca 25-100 [3,4,5] coastal Douglas-fir* P. menziesii var. menziesii 40-240 [3,51,58] western redcedar-western hemlock Thuja plicata-Tsuga heterophylla >200 [3] *fire return interval varies widely; trends in variation are noted in the species review
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Fire Management Considerations

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The current body of research provides no clear direction for using fire as a management tool for tall bluebells populations. Research (discussed above) suggests that fire does not significantly hinder tall bluebells populations and may even have positive effects. Further research is needed.
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Growth Form (according to Raunkiær Life-form classification)

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More info for the terms: geophyte, hemicryptophyte

RAUNKIAER [56] LIFE FORM:
Hemicryptophyte
Geophyte
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Habitat characteristics

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Tall bluebells shows an affinity to "rich" boreal forest sites [12]. Site descriptions are provided below.

State, Region, Province Variety, if applicable Site Characteristics Alaska (and neighboring Provinces) Alaska tall bluebells woods and riverbanks Eastwood's bluebell woods and riverbanks typical variety woods, riverbanks, in McKinley Park to 5,600 feet (1,700 m) [34] Idaho northern bluebells streamsides and wet meadows [52] riverbanks, rocky slopes, wet meadows; 5,000-8,400 feet (1,500-2,600 m) [9] Michigan ...* Coniferous swamps and woods, shaded edges of streams, rocky openings; rarely in deciduous woods [70] Montana (west-central) ... moist woods and meadows [11,19] Mt Rainier National Park ... moist places; 4,000 to 6,000 feet (1,200-1,800 m) [61] Pacific Northwest ... streambanks, wet meadows, damp thickets, and wet cliffs, open forests at all elevations [31,54] Selway-Bitterroot Mountains, ID and MT ... riverbanks to timberline [41] Canada ... damp woods [26] *variety not stated
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/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 [23]:




1 Jack pine

5 Balsam fir

12 Black spruce

13 Black spruce-tamarack

16 Aspen

18 Paper birch

37 Northern white-cedar

38 Tamarack

107 White spruce

201 White spruce

202 White spruce-paper birch

203 Balsam poplar

204 Black spruce

206 Engelmann spruce-subalpine fir

210 Interior Douglas-fir

213 Grand fir

215 Western white pine

217 Aspen

218 Lodgepole pine

222 Black cottonwood-willow

224 Western hemlock

227 Western
redcedar-western hemlock

228 Western redcedar

229 Pacific Douglas-fir

251 White spruce-aspen

252 Paper birch

253 Black spruce-white spruce

254 Black spruce-paper birch
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/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 [25]:




FRES10 White-red-jack pine

FRES11 Spruce-fir

FRES19 Aspen-birch

FRES20 Douglas-fir

FRES22 Western white pine

FRES23 Fir-spruce

FRES24 Hemlock-Sitka spruce

FRES26 Lodgepole pine

FRES28 Western hardwoods
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Habitat: Plant Associations

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

More info for the term: forest

KUCHLER [40] PLANT ASSOCIATIONS:




K002 Cedar-hemlock-Douglas-fir forest

K012 Douglas-fir forest

K013 Cedar-hemlock-pine forest

K015 Western spruce-fir forest

K093 Great Lakes spruce-fir forest

K094 Conifer bog
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/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, shrub, swamp, tundra, tussock

SRM (RANGELAND) COVER TYPES [60]:




901 Alder

904 Black spruce-lichen

905 Bluejoint reedgrass

906 Broadleaf forest

908 Fescue

917 Tall shrub swamp

918 Tussock tundra

920 White spruce-paper birch
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Immediate Effect of Fire

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Tall bluebells is likely top-killed by fire.
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Importance to Livestock and Wildlife

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There is little documentation of tall bluebell use by animals. It is a main component of the snowshoe hare summer diet in Yukon Territory [29], a known grizzly bear food plant in southern Canada and the conterminous 48 United States [16], and an important species for elk in the summer in northern Idaho [45].

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. 2006. Mertensia paniculata. 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/merpan/all.html

Key Plant Community Associations

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More info for the terms: forest, phase

Tall bluebells is a dominant species in the following boreal forest community
types of North America [22]:




  • balsam fir-cottonwood/prickly rose (Abies balsamea-Populus spp./Rosa acicularis)/tall
    bluebells phase of the white spruce-fir (Picea glauca-Abies spp.) community type




  • prickly rose-red currant/naked miterwort (Ribes triste/Mitella nuda)-tall bluebells phase
    of the black spruce (P. mariana) community type


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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Life Form

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More info for the term: forb

Forb
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Management considerations

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More info for the terms: competition, cover, frequency

Tall bluebells shows some resistance to disturbance. In British Columbia, tall
bluebells percent cover increased on
sites that were disked and then sprayed with glyphosate compared to sites that
were just disked. On undisked sites, tall bluebells percent cover was lower on the
sprayed site than the site with no treatment [10].

Tall bluebells increased or maintained pretreatment levels after white spruce harvesting on Willow Island near
Fairbanks, Alaska. The percent frequency of tall bluebells
surpassed pretreatment levels within 1 year, and percent cover was surpassed within 2 years of clearcutting.
One year after a shelterwood treatment, tall bluebells cover value remained the
same, and frequency decreased slightly [21].
Harvesting in quaking aspen stands in British Columbia significantly (P≤0.05)
increased the cover of tall bluebells on both grazed and ungrazed study areas, more so in
the latter. Greater light transmission and reduced plant competition for water
and nutrients after harvesting may increase tall bluebells cover. The
percent cover of tall bluebells after treatments is detailed below [39].

 
Ungrazed treatment
Grazed treatment
Unharvested
0.5
3.7
Harvested
4.3
5.9

Conversely, there is evidence that tall bluebells is intolerant to
logging disturbance. In northeastern British Columbia tall bluebells
is strongly associated with unlogged plant communities.
It showed a reduction in frequency after clearcutting [28].

Herbicides: On boreal quaking aspen stands
in Alberta, tall bluebells percent cover was reduced
after applications of the herbicide hexazinone. The herbicide was applied in a
3-year-old regenerating quaking aspen clearcut to determine the effects of
spraying on the compositional and structural development of vegetation [64].
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Phenology

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Flowering dates for tall bluebells are provided below.

State or province Anthesis period Idaho May to August [52] Ontario June to September [36] Yukon May to June [32]
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Plant Response to Fire

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More info for the terms: caudex, seed, wildfire

Tall bluebells sprouts from the caudex, rhizomes, and roots after fire. It is known to establish on burned soils, likely from an off-site seed source [2,47,72].
Tall bluebells after a wildfire in Yukon-Charley Rivers National Park. Photo courtesy of USDI, National Park Service.
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Post-fire Regeneration

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More info for the terms: fire regime, geophyte, herb, rhizome, root crown, secondary colonizer, seed

POSTFIRE REGENERATION STRATEGY [62]:
Rhizomatous herb, rhizome in soil
Caudex/herbaceous root crown, growing points in soil
Geophyte, growing points deep in soil
Secondary colonizer (on-site or off-site seed sources)

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"

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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Regeneration Processes

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More info for the terms: adventitious, seed, tundra, tussock

Tall bluebells regenerates mostly by vegetative means [29,38]. Morris [50] states that tall bluebells is "clonal, but nonspreading". Tall bluebells reproduces from ramets that typically remain tightly clustered around the parent plant, possibly limiting clonal spreading [18,29]. Hicks and Turkington [29] mention sprouting from rhizomes. Mann and Plug [47] state that excavated tall bluebell individuals were spreading laterally by adventitious roots, and it is on this basis that they inferred its capability to reproduce by sprouting. It is also likely that tall bluebells regenerates from seed. Further research is needed on the regeneration of tall bluebells from seed.

Pollination: Bumble bees are the only documented pollinator of tall bluebells [46,50].

Breeding system: No information is available on this topic.

Seed production: Each flower may produce up to 4 single-seeded nutlets [50].

Seed dispersal: No information is available on this topic.

Seed banking: Soil excavated from a tussock tundra site at Eagle Creek, Alaska, was tested in the laboratory for viable seeds. Tall bluebells was part of the aboveground tundra vegetation but did not germinate in the laboratory [48], suggesting either that it does not have a great capacity for seed banking or that its germination requirements were not met during testing.

Germination: No information is available on this topic.

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

Vegetative regeneration: Tall bluebells regenerates vegetatively from rhizomes [29].

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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/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 [8]:




1 Northern Pacific Border

2 Cascade Mountains

5 Columbia Plateau

8 Northern Rocky Mountains
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

States or Provinces

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(key to state/province abbreviations)
UNITED STATES AK CT IA ID MI MN MT OR WA WI
CANADA AB BC MB NT NU ON PQ SK YK
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Successional Status

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More info for the terms: climax, cover, frequency, relative frequency, shrub, succession, tundra

Tall bluebells is a shade tolerant species [38,44] that occurs in early and late-seral communities. Although generally most common in mid-succession, it has been observed in early successional boreal communities in Alaska and Canada after fire, clearcutting, and logging/burning [15,24,57,59,63]. Mean frequency and cover of tall bluebells was greatest on newly burned white spruce stands in Alaska, and tall bluebells maintained mean frequency and cover throughout all other stages of succession [24].

Tall bluebells is often present in early seral stages and increases in frequency and cover over time. Average percent cover of tall bluebells increased, though not significantly (P=0.516), within a regenerating quaking aspen (Populus tremuloides) stand in Alberta 3, 5, 9, and 20 years after clearcutting. Percent cover was 1%, 2%, 1%, and 4%, respectively [63]. On 18- and 19-year-old black spruce plantations, tall bluebells had mean relative frequency of 3%. Twenty years later at the same site, mean relative frequency was 39% [35]. Tall bluebells was not present in the pioneer stage (25 to 35 years) on gravel outwash from the Muldrow Glacier in Alaska. Cover and frequency increased throughout the meadow (100 years after glacial scour), early shrub (150-200 years), and late shrub (200-300 years) stages, with the greatest tall bluebells cover and frequency during the latter. There was no evidence of tall bluebells in climax tundra (5,000-9,000 years) [68]. Tall bluebells percent frequency and cover increased through the 1st 3 stages of succession recorded for the Chena River floodplain near Fairbanks, Alaska, but tall bluebells was not present in later successional and climax communities. Percent frequency and cover for tall bluebells are provided below [69].

Successional stage Percent frequency Percent cover 15-year-old Alaska willow (Salix alaxensis) stand 10 <1 50-year-old balsam poplar (Populus balsamifera) stand 20 1 120-year-old white spruce stand 40 2 220-year-old white spruce-black spruce stand 0 0 climax black spruce/sphagnum (Sphagnum spp.) stand 0 0
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Taxonomy

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The scientific name of tall bluebells is Mertensia paniculata (Ait.) G.
Don (Boraginaceae) [11,19,26,30,34,37,41,70]. There are currently 4
recognized varieties of tall bluebells. Throughout this review, varieties will be
identified by their common names.

Mertensia paniculata var. alaskana (Britt.) Williams [1,34], Alaska tall bluebells

Mertensia paniculata var. borealis (Macbr.) Williams [9,30,31,42], northern bluebells

Mertensia paniculata var. eastwoodae (Macbr.) Hultén [34], Eastwood's bluebells

Mertensia paniculata var. paniculata [30,34], tall bluebells (typical variety)

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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Value for rehabilitation of disturbed sites

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Tall bluebells was planted for restoration of alpine and subalpine areas disturbed by construction, visitor impact, and mining in Denali National Park, Alaska. Tall bluebells plants were propagated from seed under greenhouse conditions and subsequently planted into a raised nursery bed. The plants were "large, vigorous, and flowering" within 1 year of transplanting [17].
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Reeves, Sonja L. 2006. Mertensia paniculata. 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/merpan/all.html

Mertensia paniculata

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Mertensia paniculata, also known as the tall lungwort, tall bluebells, or northern bluebells, is an herb or dwarf shrub with drooping bright-blue, bell-shaped flowers. It is native to northwestern North America and the Great Lakes.

Distribution

Mertensia paniculata naturally occurs in the temperate zone of North America, and is known to thrive within the boreal forests.[2] Specifically, the northern bluebell can be found in Canada, including southern British Columbia. Within the United States, the plant can be seen in Alaska, as well as the Olympic Mountains, stretching east through Oregon to Idaho and western Montana.[3] According to the PLANTS database, M. paniculata are also spotted as far east as Michigan, Wisconsin, and Minnesota.[4]

Habitat and ecology

Mertensia paniculata thrives in moist wooded or meadow areas. It is a shade-tolerant species and is present in early and late-seral communities. While it is most common in mid-succession, it has been spotted in areas in Alaska and Canada after events such as fire or logging, as an early successional community. The northern bluebell seems to have the ability to grow once more after said events due to sprouting from buried rhizomes or from vegetative parts from the surface.[5] It can also flourish under soil that is mesic,[6] has a low temperature, and has limited nutrient availability.[7] It is a perennial that, according to studies in the Yukon region, is a dominant species with precipitation of 230 mm annually, with an average temperature of −3° Celsius.[8] The months in which the flowers bloom depend on the area in which it originates, but mainly the flowering dates range from May to September.[9]

Illustration of M. paniculata from PLANTS database

It is found on the lower Yukon in abundance. It grows around homes and dry sunny areas near homes, in meadows and wherever there is less wind and more sunlight.

Morphology

Individuals of this species can be considered an herb-forb or a subshrub. It can sprout one to several erect stems with little to no hair at all from one long root. The stem can range from .1 to .7 meters in length. Basal leaves vary between .05 m and .2 m longitudinally and .025 m to .1 m laterally and come in a variety of shapes, including wide, elliptic-lanceolate to ovate-subcordate, eventually tapering to an acute to acuminate point at the apex. The underside of the leaf can be sparsely populated with hairs or completely smooth, and the upper surface can contain short, stiff, and slender bristles or range to completely smooth as well. Leaves are pinnately veined, simple, with petioles ranging from .1-.25 m long, becoming winged traveling up the stem of the plant. Furthermore, the leaves higher on the plant range from .05 to .18 m longitudinally and from .01 to .08 m laterally and are broad, ovate to lanceolate, with acuminate ends. Leaves are arranged in an alternate fashion as it ascends the plant. Flowers are branched on one side, forming a spiral-shaped inflorescence, otherwise known as a scorpioid cyme.[2]

Flowers, fruit, and reproduction

The inflorescence is branched and uncrowded and the fruit consists of one to four nutlets (Mount Rainier National Park).

The bisexual flower of M. paniculata has five blue petals making up the corolla, which are commonly pink when young. Sometimes, but rarely, the corolla is white on a mature flower. The shape of the five sepals that form the calyx is linear-lanceolate and cilia are present on the margin of the sepal. The underside of the sepal can range to having either have little to no hairs or having short, stiff hairs close together, with a bristle-like texture. The tube of the northern bluebell is .0045–.007 m long, with the anthers measuring about .0022–.0033 m in length, and the style as long as or surpassing the length of the corolla.[2] The fruit of the tall lungwort are 1 to 4 small, wrinkled, single-seeded nutlets that are .0025–.005 m long, which appear in a cluster.[6] The species also appear to be able to reproduce from a member of a clone that stays clustered around the parent plant.[10] It has been observed that the plants spread laterally by adventitious roots after fire and it has been inferred that the species is capable of reproducing by sprouting.[11]

Usage

Food and medicine

While the tall bluebell's organs are not edible whole, it has been used in the past as a pot-herb in the north and in areas of Scotland, due to its place in the borage family.[12] It also has been used for medicinal purposes. The dried leaves of the plant could be made into an herbal tea to stimulate the respiratory system.[13]

References

  1. ^ "Mertensia paniculata (Aiton) G. Don". Tropicos.org. Missouri Botanical Garden. 2013. Retrieved 28 July 2013.
  2. ^ a b c Elliott-Fisk, Deborah (1988). Barbour, Michael (ed.). "The boreal forest". North American Terrestrial Vegetation. Cambridge, NY: Cambridge University Press: 33–62.
  3. ^ Abrams, Leroy (1951). Illustrated Flora of the United States - Washington, Oregon, and California. Stanford, California: Stanford University Press. p. 545.
  4. ^ USDA, NRCS. "The PLANTS Database". National Plant Data Team. Retrieved 4 July 2011.
  5. ^ Wang, Geoff; Kevin Kemball (2004). "The effect of fire severity on early development of understory vegetation following a stand replacing wildfire". Session 3B - Fire Effect on Flora: Part 2. 2nd international wildland fire ecology and fire management congress: Proceedings; 2003 November 19; Orlando, FL: 11.
  6. ^ a b Douglas, George (1998). Illustrated Flora of British Columbia. Volume 2: Dicotyledons (Balsaminaceae Through Cucurbitaceae). Victoria: B.C. Ministry of Environment, Lands & Parks and B.C. Ministry of Forests. p. 401.
  7. ^ Arii, Ken (1996). Factors Restricting Plant Growth In A Boreal Forest Understory: A Field Test of the Relative Importance of Abiotic and Biotic Factors (PDF) (M.Sc. thesis). University of British Columbia. Retrieved July 5, 2011.
  8. ^ John, Elizabeth; Roy Turkington (August 1997). "A 5-Year Study of the Effects of Nutrient Availability and Herbivory on Two Boreal Forest Herbs". Journal of Ecology. 85 (4): 419–430. doi:10.2307/2960566. JSTOR 2960566.
  9. ^ Hoefs, Manfred (1979). "Flowering plant phenology at Sheep Mountain, southwest Yukon Territory". Canadian Field-Naturalist. 93 (2): 183–187.
  10. ^ Hicks, Samantha; Roy Turkington (2000). "Compensatory growth of three herbaceous perennial species: the effects of clipping and nutrient availability". Canadian Journal of Botany. 78 (6): 759–767. doi:10.1139/cjb-78-6-759.
  11. ^ Mann, Daniel; Lawrence Plug (1999). "Vegetation and soil development at an upland taiga site, Alaska". Écoscience. 6 (2): 272–285. doi:10.1080/11956860.1999.11682528.
  12. ^ Hibberd, Shirley (1900). Familiar Garden Flowers, Volume 3. Cassell, Petter, Galpin & Co./Oxford University. p. 160.
  13. ^ Runesson, Ulf. "Mertensia paniculata - Northern Bluebell". Faculty of Natural Resources Management - Lakehead University. Archived from the original on 3 December 2012. Retrieved 7 July 2011.

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Mertensia paniculata: Brief Summary

provided by wikipedia EN

Mertensia paniculata, also known as the tall lungwort, tall bluebells, or northern bluebells, is an herb or dwarf shrub with drooping bright-blue, bell-shaped flowers. It is native to northwestern North America and the Great Lakes.

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