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Eastern Hemlock

Tsuga canadensis (L.) Carrière

Comments

provided by eFloras
Numerous cultivars of Tsuga canadensis have been developed, including compact shrubs, dwarfs, and graceful trees. Wood of the species tends to be brittle and inferior to that of the other North American hemlocks.

Eastern hemlock ( Tsuga canadensis ) is the state tree of Pennsylvania.

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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
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Description

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Trees to 30m; trunk to 1.5m diam.; crown broadly conic. Bark brownish, scaly and fissured. Twigs yellow-brown, densely pubescent. Buds ovoid, 1.5--2.5mm. Leaves (5--)15--20(--25)mm, mostly appearing 2-ranked, flattened; abaxial surface glaucous, with 2 broad, conspicuous stomatal bands, adaxial surface shiny green (yellow-green); margins minutely dentate, especially toward apex. Seed cones ovoid, 1.5--2.5 ´ 1--1.5cm; scales ovate to cuneate, 8--12 ´ 7--10mm, apex ± round, often projected outward. 2 n =24.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
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eFloras

Habitat & Distribution

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Moist rocky ridges, ravines, and hillsides; 600--1800m; N.B., N.S., Ont., P.E.I., Que.; Ala., Conn., Del., Ga., Ind., Ky., Maine, Md., Mass., Mich., Minn., N.H., N.J., N.Y., N.C., Ohio, Pa., R.I., S.C., Tenn., Vt., Va., W.Va., Wis.
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Synonym

provided by eFloras
Pinus canadensis Linnaeus, Sp. Pl. ed. 2, 2: 1471. 1763
license
cc-by-nc-sa-3.0
copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
project
eFloras.org
original
visit source
partner site
eFloras

Broad-scale Impacts of Plant Response to Fire

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

The Research Project Summary Early postfire effects of a prescribed fire
in the southern Appalachians of North Carolina
provides information on
prescribed fire and postfire response of plant community species, including
eastern hemlock, that was not available when this species review was
originally written.
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cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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/

Common Names

provided by Fire Effects Information System Plants
eastern hemlock
Canada hemlock
hemlock spruce
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cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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
More info for the term: cover

Eastern hemlock provides cover to ruffed grouse, wild turkey, fishers,
and other wildlife [4,20].  It provides excellent thermal protection and
snowfall interception for moose and white-tailed deer in the winter
[2,17].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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
Eastern hemlock is a native, evergreen conifer with heavily foliaged and
upsweeping branches.  At maturity, it is commonly 60 to 70 feet (18-21
m) tall and 24 to 48 inches (61-122 cm) in d.b.h.  One of the largest
eastern hemlock recorded was 175 feet (53 m) tall and 76 inches (193 cm)
in d.b.h.  It reaches ages in excess of 800 years.  Eastern hemlock
roots are shallow and widespreading [20,26].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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
In the United States, eastern hemlock occurs throughout New England, the
mid-Atlantic states, and the Lake States, and extends south in the
Appalachian Mountains to northern Georgia and Alabama and west from the
mountains into Indiana, western Ohio, and western Kentucky.  At its
northern limit, eastern hemlock ranges along the southern border of
Canada from southern Ontario to Cape Breton Island, Nova Scotia [20,35].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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 terms: fire regime, forest, litter, tree

Eastern hemlock is very susceptible to fire because of its thin bark,
shallow roots, low-branching habit, and heavy litter deposits [20,51].
It is possibly the most fire-sensitive mesophytic tree species in its
range [51].

Eastern hemlock usually escapes fire because it occurs in moist habitats
and is often associated with hardwoods which do not readily burn.  If a
fire starts in a cutover area, a windfall area, or an area with dead
standing timber, it may carry into a northern hardwoods forest if there
is strong wind [18].  In Michigan, the average return time for severe
crown fires in the hemlock-white pine-northern hardwoods type is
estimated to be about 1,400 years [63].  In northeastern Maine, the
average return interval for fire in spruce-fir forests in which eastern
hemlock is a minor component is about 800 years [37].

Vogl [61] considers eastern hemlock a fire-initiated species rather than
a fire-independent species because it benefits from fire-prepared
seedbeds.  However, suggestions that fire promotes regeneration of
eastern hemlock are not well documented.  Given the difficulties in
accurate age estimates because of heart rot, Rogers [51] suggests that
even-aged eastern hemlock forests that regenerated after fire may
actually be uneven-aged.

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
Carey, Jennifer H. 1993. Tsuga canadensis. 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 term: phanerophyte

Phanerophyte
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cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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 terms: peat, shrub, swamp, tree

At its western and southern limits, eastern hemlock is confined to moist
cool valleys, moist flats, northern and eastern slopes, coves, benches,
and ravines.  In the northern part of its range, it tolerates drier and
warmer sites.  Eastern hemlock also occurs at swamp borders provided
peat and muck soils are shallow [14,20,40,65].

Favorable eastern hemlock sites are moist to very moist with good
drainage.  Eastern hemlock grows in a wide variety of acidic soils;
textures include sandy loams, loamy sands, and silty loams with gravel
of glacial origin in the upper profile [14,20].

While generally considered a moisture-demanding species, eastern hemlock
grows on dry sites protected from fire, such as rocky ledges [22].  Two
types of eastern hemlock have been described:  one grows in mesophytic
habitats and one on subxeric slopes [30].  The types cannot be termed
ecotypes, however, because of incomplete habitat differentiation.
Eastern hemlock growing on "subxeric" slopes may actually be receiving
moisture from seeps [51].

In the northeastern United States, eastern hemlock grows at elevations
ranging from sea level to 2,400 feet (730 m).  In the southern
Appalachian Mountains it grows from 2,000 to 5,000 feet (610-1,520 m).
In the Allegheny Plateau region of New York, Pennsylvania, and Ohio, it
grows from 1,000 to 3,000 feet (300-910 m) [13,20,34].

Understory associates are scarce because of acidic infertile humus, low
light, and cool conditions [14,34].  Shrub and small tree associates
that occur in canopy gaps include sweet birch (Betula lenta), striped
maple (Acer pensylvanicum), mountain maple (A. spicatum), hobblebush
(Viburnum alnifolium), mapleleaf viburnum (V.  acerifolium), mountain
winterberry (Ilex montana), rhododendron (Rhododendron spp.),
mountain-laurel (Kalmia latifolia), and witch hazel (Hamamelis
virginiana).  Herbs can include Canada mayflower (Maianthemum
canadense), star flower (Trientalis borealis), common woodsorrel (Oxalis
montana), and goldthread (Coptis groenlandica).  Other associated
species include clubmosses (Lycopodium spp.), bracken (Pteridium
aquilinum), woodfern (Dryopteris spp.), and sedges (Carex spp.).  Common
mosses include Dicranium spp. and Polytrichum spp. [14,20,32,45,65].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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

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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):

     5  Balsam fir
    17  Pin cherry
    18  Paper birch
    19  Gray birch - red maple
    20  White pine - northern red oak - red maple
    21  Eastern white pine
    22  White pine - hemlock
    23  Eastern hemlock
    24  Hemlock - yellow birch
    25  Sugar maple - beech - yellow birch
    26  Sugar maple - basswood
    27  Sugar maple
    28  Black cherry - maple
    30  Red spruce - yellow birch
    31  Red spruce - sugar maple - beech
    32  Red spruce
    33  Red spruce - balsam fir
    34  Red spruce - Fraser fir
    35  Paper birch - red spruce - balsam fir
    37  Northern white-cedar
    39  Black ash - American elm - red maple
    44  Chestnut oak
    52  White oak - black oak - northern red oak
    53  White oak
    57  Yellow-poplar
    58  Yellow-poplar - eastern hemlock
    59  Yellow-poplar - white oak - northern red oak
    60  Beech - sugar maple
    97  Atlantic white-cedar
   108  Red maple
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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

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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):

   FRES10  White - red - jack pine
   FRES11  Spruce - fir
   FRES15  Oak - hickory
   FRES18  Maple - beech - birch
   FRES19  Aspen - birch
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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

   K093  Great Lakes spruce - fir forest
   K094  Conifer bog
   K095  Great Lakes pine forest
   K096  Northeastern spruce - fir forest
   K097  Southeastern spruce - fir forest
   K103  Mixed mesophytic forest
   K104  Appalachian oak forest
   K106  Northern hardwoods
   K107  Northern hardwoods - fir forest
   K108  Northern hardwoods - spruce forest
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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
More info for the terms: ground fire, presence

Low-severity fire readily kills seedlings and saplings of eastern
hemlock, and may also kill larger trees.  A low-severity ground fire in
a northern hardwoods community in south-central New York killed 93
percent of the eastern hemlock saplings.  Sixty percent of the mature
eastern hemlock died or were badly injured as a result of the fire [58].
The presence of fire scars indicates that larger trees have thick enough
bark to survive low-severity surface fires [18,36].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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
Dense stands of eastern hemlock provide excellent wildlife habitat [20].
Cove forests in the southern Appalachian Mountains provide nesting
habitat for many species of birds.  The black-throated blue warbler,
black-throated green warbler, and blackburnian warbler are especially
abundant in virgin eastern hemlock cove forests [25].

Large eastern hemlocks can be climbed by small black bear cubs.  In
northeastern Minnesota, black bear mothers and cubs spent more than 95
percent of the time in April and May within 600 feet (183 m) of either
an eastern hemlock or an eastern white pine (Pinus strobus) larger than
20 inches (51 cm) in d.b.h. [50].

Eastern hemlock has high cavity value for wildlife [12].  Large hollow
trees are commonly used as dens by black bears [49].

The seeds are eaten by birds and mammals [13], and in the winter the
foliage is browsed by white-tailed deer, moose, and snowshoe hares
[2,59].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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, natural

Eastern hemlock occurs as a dominant or codominant in coniferous and
mixed-hardwood forests.  It is often the only conifer present in mixed
mesophytic forests of the eastern United States [40].

Publications listing eastern hemlock as codominant or dominant are as
follows:

The natural forests of Maryland: an explanation of the vegetation map
   of Maryland [7]
A multivariate analysis of forest communities in the western Great Smoky
   Mountains National Park [9]
The vegetation of Wisconsin [10]
The principal plant associations of the Saint Lawrence Valley [11]
Field guide: forest habitat types of northern Wisconsin [32]
A classification of the deciduous forest of eastern North America [42]
The natural communities of South Carolina [45]
Forest associations in the Harvard Forest [55]
Vegetation of the Great Smoky Mountains [65]
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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: tree

Tree
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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 terms: cover, forest, scarification, selection, series, tree

Multiple removal cuttings are the best method for regenerating eastern
hemlock.  Suddenly released seedlings often die, and a series of
removals releases hemlock more slowly [28].  On moist sites, a two-cut
shelterwood system leaving about 50 percent cover may be adequate.  On
drier sites, a three-cut system is appropriate, initially leaving 70 to
80 percent crown cover and 50 percent after the second cut [62].  If too
few residual trees are left, they may die when exposed, and they are
subject to windthrow [28].  Scarification of seedbeds and removal of
competing hardwoods may be necessary [20].  Eastern hemlock regeneration
must be at least sapling size when released if it is to compete
successfully with uncontrolled hardwoods [29].  Single tree selection is
also an effective method to harvest and regenerate eastern hemlock [62].

Effective reproduction may be absent in areas with high deer populations
[3,10].  Regeneration in the Porcupine Mountains in Michigan has
declined over the last several decades because of white-tailed deer
browsing in the winter [17].  In the Allegheny National Forest in
Pennsylvania, the eastern hemlock-northern hardwoods forest type covered
83.4 percent of the land in 1800 and only 15.8 percent in 1986.
Extensive harvesting, fire, and overbrowsing are responsible for the
decline [64].

Numerous insects attack eastern hemlock, but only a few are of economic
importance cause sporadic or local mortality [62].  Mortality
usually occurs following complete defoliation by insects [43,62].

Eastern hemlock seedlings are sensitive to damping-off fungi, root rots,
and stem and needle rusts [20].

Eastern hemlock appears to be resistant to ozone [21].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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  CT  DE  GA  IN  KY  ME  MD  MA  MI
     MN  NH  NJ  NY  NC  OH  PA  RI  SC  TN
     VT  VA  WV  WI  NB  NS  ON  PE  PQ
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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
From 1880 to 1930, eastern hemlock was extensively harvested for its
bark which is a source of tannin [64]. 

Eastern hemlock is planted as an ornamental [20].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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
More info for the term: hardwood

In the winter, eastern hemlock browse is moderately preferred by moose
and highly preferred by white-tailed deer [2,10].  In the summer,
white-tailed deer prefer hardwood sprouts and seedlings to eastern
hemlock [44].  The seeds of eastern hemlock are not as preferred by
white-footed mice, red-backed voles, and meadow voles as red pine (Pinus
resinosa) and white pine seeds [1].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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 for the term: seed

Eastern hemlock male strobili open and pollen is dispersed in late April
to early June, depending on locality.  This is usually 2 weeks after the
leaf buds open.  Fertilization is complete in about 6 weeks, and cones
reach full size in late August or early September.  The cones open in
mid-October, but seed dispersal may extend into the winter [20].  Cones
close in wet weather and open again in subsequent dry weather,
prolonging seed dispersal.  Germination occurs in the spring [10].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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 term: forest

Eastern hemlock appears to invade burned sites over time.  In the Pisgah
Forest in southwestern New Hampshire, 80 percent of old-growth hemlock
germinated within the first 37 years after a major fire in 1665 [23].
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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: root crown, secondary colonizer, tree

   Tree without adventitious-bud root crown
   Secondary colonizer - off-site seed
license
cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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

provided by Fire Effects Information System Plants
More info for the terms: competition, cover, density, litter, seed

Trees begin producing seed when they are 20 to 30 years old.  Eastern
hemlocks older than 450 years still produce large seed crops.  This
species bears cones every year, and large crops are frequent, usually
every 3 to 4 years.  The small winged seeds are dispersed by gravity and
wind; most fall within one-tree-height distance from the source [20,54].

The seeds are partially dormant and germinate best when stratified for
about 10 weeks at or slightly above freezing.  Germination occurs at a
range of temperatures; seeds from the northern portion of its range
germinate at lower temperatures than seeds from the southern portion
[20,54].  Seeds do not remain viable if they do not germinate the first
spring after seedfall [38].

Seeds germinate best on moist substrates, such as rotten wood, mineral
soil, mineral soil mixed with humus, well-decomposed litter, and moss
mats [14,62].  The number of seedlings established on rotten logs and
stumps increases as the wood decays and the moss cover increases.
Seedlings commonly establish on "tip-up mounds" formed by fallen trees
[10].  Seedlings grow slowly and cannot tolerate full sunlight until
fully established, usually when they are 3 to 5 feet (0.9-1.5 m) tall
[20].

Eastern hemlock regeneration appears to be periodic and is influenced by
fire, windthrow, drought, and stand conditions.  A young dense stand may
exclude regeneration for many years because of severe root competition
in the upper soil layers, dense low shade, and dry acidic litter
[27,56].  Hemlock regeneration is present in the understory of stands
with a parent overstory density of up to 140 square feet per acre (32 sq
m/ha) but is most abundant when eastern hemlock comprises 80 to 100
square feet per acre (18-23 sq m/ha) of the overstory [31].

Eastern hemlock does not sprout and layers only rarely [20].
license
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bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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 for the terms: climax, forest, litter

Eastern hemlock is very shade tolerant [5].  Seedlings survive in as
little as 5 percent of full light [14].  Individuals are able to survive
several hundred years of suppression, and many show numerous growth
releases and suppressions [6].  Saplings less than 2 inches (5 cm) in
d.b.h. may be more than 100 years old [10].

Seedlings are able to establish under the canopy of mature individuals.
Eastern hemlock establishes under dense sugar maple canopies and can
replace that species [39].  Eastern hemlock uniquely modifies
semipermanent soil properties, such as acidity, which favors its
reproduction.  Opportunities to establish in a mature forest increase
over time as nurse logs and tip-up mounds accumulate [51].

The general designation of eastern hemlock as a climax species has been
questioned [22,41].  In some old-growth eastern hemlock stands, the
smaller size classes of hemlock are being replaced by American beech
(Fagus grandifolia) and sugar maple [41].  Because of this lack of
regeneration, Hemond and others [22] suggest that eastern hemlock
requires disturbance to perpetuate itself.

In contrast, other authors suggest that disturbance is responsible for
the lack of regeneration in mature hemlock forests [3,6,51].
White-tailed deer populations have increased since presettlement times
because logging of virgin forests opened up habitat, predators declined,
and the deer were protected.  Deer often consume all eastern hemlock
seedlings and saplings in the winter.  Where deer populations are low,
eastern hemlock appears to be able to reproduce in its own shade and
become a component of a self-perpetuating homogenous climax forest [3].

Eastern hemlock requires partial shade for establishment and is a late
colonizer of disturbed sites [24].  In the Pisgah Forest in southwestern
New Hampshire, 80 percent of old-growth eastern hemlock established
within 37 years of disturbance.  Hardwoods grew rapidly into the canopy
while eastern hemlock grew slowly as shade-tolerant saplings.  Eastern
hemlock extended into the canopy following subsequent disturbance [23].

The understory population of eastern hemlock readily takes advantage of
canopy gaps.  Eastern hemlock increased in importance as American
chestnut (Castanea dentata) declined from chestnut blight [8].  It is
currently replacing American beech where that species is succumbing to
beech bark disease [53].  Eastern hemlock is not successful in
regenerating in canopy gaps in areas such as the New York Botanical
Forest, where the occasional light arson fire, trampling, and other
urban stresses kill seedlings.  In addition, the removal of fallen logs
in the forest decreases the amount of adequate substrate for germination
[52].

The slow invasion of oak-dominated sites by eastern hemlock appears to
be related to heavy leaf litter and the absence of favorable seedbed
conditions [22].
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bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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 for eastern hemlock is Tsuga
canadensis (L.) Carr. [35]. Fernald [15] recognizes a dwarf form, T.
canadensis forma parvula Vict. and Rousseau, that grows in mats up to 3
feet (1 m) high in Quebec and New England.
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cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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/

Wood Products Value

provided by Fire Effects Information System Plants
Eastern hemlock wood is of low value because of brittleness and abundant
knots [26].  It is used for pulp, light framing, sheathing, roofing,
subflooring, and boxes and crates [20].
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cc-publicdomain
bibliographic citation
Carey, Jennifer H. 1993. Tsuga canadensis. 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/

Physical Description

provided by USDA PLANTS text
Tree, Evergreen, Monoecious, Habit erect, Trees without or rarely having knees, Tree with bark rough or scaly, Young shoots 3-dimensional, Buds not resinous, Leaves needle-like, Leaves alternate, Needle-like leaf margins finely serrulate (use magnification or slide your finger along the leaf), Leaf apex obtuse, Leaf apex mucronulate, Leaves < 5 cm long, Leaves < 10 cm long, Leaves yellow-green above, Leaves not blue-green, Needle-like leaves flat, Needle-like leaves not twisted, Needle-like leaf habit erect, Needle-like leaf habit drooping, Needle-like leaves per fascicle mostly 1, Needle-like leaf sheath early deciduous, Needle-like leaf sheath persistent, Twigs pubescent, Twigs densely pubescent, Twigs not viscid, Twigs with peg-like projections or large fascicles after needles fall, Berry-like cones orange, Woody seed cones < 5 cm long, Bracts of seed cone included, Seeds brown, Seeds winged, Seeds unequally winged, Seed wings prominent, Seed wings equal to or broader than body.
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Steffi Ickert-Bond
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Tsuga canadensis

provided by wikipedia EN

An Eastern Hemlock branch at the Kortright Centre for Conservation.

Tsuga canadensis, also known as eastern hemlock,[3] eastern hemlock-spruce,[4] or Canadian hemlock, and in the French-speaking regions of Canada as pruche du Canada, is a coniferous tree native to eastern North America. It is the state tree of Pennsylvania.[5] Eastern hemlocks are widespread throughout much of the Great Lakes region, the Appalachian Mountains, the Northeastern United States, and Maritime Canada. They have been introduced in the United Kingdom and mainland Europe, where they are used as ornamental trees.

Eastern hemlock populations in North America are threatened in much of their range by the spread of the invasive Hemlock woolly adelgid, which infests and eventually kills trees. Declines in population from hemlock wooly adelgid infestation have led to Tsuga canadensis being listed as Near Threatened on the IUCN Red List.

Eastern hemlocks are long lived trees, with many examples living for more than 500 years. They can grow to heights of more than 30 metres (100 ft), and are tolerant of shade, moist soil, and slopes. Hemlock wood is used in construction, and for railroad ties. Historically its bark was an important source of tannin for the leather tanning industry.[6] Eastern hemlocks are popular as ornamental trees, thanks to their tolerance of a wide variety of soil and light conditions, as well as their characteristic drooping branches.

Description

A line drawing of the leaves and cones from Britton and Brown's 1913 Illustrated flora of the northern states and Canada

The eastern hemlock grows well in shade and is very long lived, with the oldest recorded specimen, found in Tionesta, Pennsylvania, being at least 554 years old.[7] The tree generally reaches heights of about 31 m (102 ft),[5] but exceptional trees have been recorded up to 53 m (174 ft).[8] The diameter of the trunk at breast height is often 1.5 m (4 ft 11 in), but again, outstanding trees have been recorded up to 1.75 m (5 ft 9 in).[9] The trunk is usually straight and monopodial, but very rarely is forked.[10] The crown is broadly conic, while the brownish bark is scaly and deeply fissured, especially with age.[5] The twigs are a yellow-brown in color with darker red-brown pulvini, and are densely pubescent. The buds are ovoid in shape and are very small, measuring only 1.5 to 2.5 mm (0 to 18 in) in length. These are usually not resinous, but may be slightly so.[5][10]

The leaves are typically 15 to 20 mm (0.59 to 0.79 in) in length, but may be as short as 5 mm (0.20 in) or as long as 25 mm (1 in). They are flattened and are typically distichous, or two-ranked. The bottom of the leaf is glaucous with two broad and clearly visible stomatal bands, while the top is a shiny green to yellow-green in color. The leaf margins are very slightly toothed, especially near the apex. The seed cones are ovoid in shape and typically measure 1.5 to 2.5 cm (58 to 1 in) in length and 1.0 to 1.5 cm (38 to 58 in) in width. The scales are ovate to cuneate in shape and measure 8 to 12 mm (38 to 12 in) in length by 7.0 to 10 mm (14 to 38 in) in width. The apex is more or less rounded and is often projected outward. Twenty-four diploid chromosomes are present within the trees' DNA.[5][10]

Wood

The wood is soft, coarse-grained, and light buff in color. Air-dried, a cubic foot (0.028 m3) weighs 28 pounds (13 kg). The lumber is used for general construction and crates. Because of its unusual power of holding spikes, it is also used for railroad ties. Untreated, the wood is not durable if exposed to the elements. As a fuel, it is low in value. The wood is also a source of pulp for paper manufacturing.[11]

Distribution and habitat

Stand of eastern hemlock and eastern white pine in Tiadaghton State Forest, Pennsylvania; note the hemlocks' deeply fissured bark

T. canadensis occurs at sea level in the north of its distribution,[10] but is found primarily at elevations of 600–1,800 m (2,000–5,900 ft). It ranges from northeastern Minnesota eastward through southern Quebec and into Nova Scotia, and south in the Appalachian Mountains to northern Georgia and Alabama.[5][12] Disjunct populations occur in the Piedmont region, northern Alabama, western Ohio and into Indiana, as well as western Wisconsin and eastern Minnesota.[10][13] In Canada, it is present in Ontario and all provinces to the east except Newfoundland and Labrador.[5] Its range completely overlaps that of the closely related Tsuga caroliniana.[14]

It is found primarily on rocky ridges, ravines, and hillsides with relatively high levels of moisture.[5]

Climate

Eastern hemlock is generally confined to areas with highland climates, with cool and humid conditions. Precipitation in the areas where it grows is typically 740 mm (29 in) to more than 1,270 mm (50 in) per year. The lower number is more typical of northern forests that receive heavy snowfall; the higher number is common in southerly areas with high summer rainfall. Near the Atlantic coast and in the southern Appalachians where the trees often reach their greatest heights, annual rainfall often exceeds 1,520 mm (60 in). In the north of its range, the temperatures in January average −12 °C (10 °F), while in July they average only 16 °C (61 °F). In these areas, the frost-free season can last fewer than 80 days. In contrast, the southern end of the range experiences up to 200 days without frost and January temperatures as high as 6 °C (43 °F).[14]

Hemlock boughs in the autumn, shedding older foliage

Hemlock woolly adelgid

Shoot infested with hemlock woolly adelgid

The species is currently threatened by the hemlock woolly adelgid (Adelges tsugae), a sap-sucking bug introduced from East Asia to the United States in 1924, and first found in the native range of eastern hemlock in the late 1960s.[15] The adelgid has spread very rapidly in southern parts of the range once becoming established, while its expansion northward is much slower. Virtually all the hemlocks in the southern Appalachian Mountains have seen infestations of the insect within the last five to seven years, with thousands of hectares of stands dying within the last two to three years. Attempts to save representative examples on both public and private lands are on-going. A project named "Tsuga Search", funded by the Great Smoky Mountains National Park, is being conducted to save the largest and tallest remaining eastern hemlocks in the Park. Through Tsuga Search, hemlocks have been found with trunk volumes up to 44.8 m³ within the park,[16] making it the largest eastern evergreen conifer, eclipsing in volume both eastern white pine (Pinus strobus) and loblolly pine (Pinus taeda). The tree is currently listed as a near threatened species in the IUCN Red List, but this is based largely on its wide distribution and because the adelgid populations have not reached the northern areas of its range.[1]

A 2009 study conducted by scientists with the U.S. Forest Service Southern Research Station suggests the hemlock woolly adelgid is killing hemlock trees faster than expected in the southern Appalachians, and rapidly altering the carbon cycle of these forests. According to Science Daily, the pest could kill most of the region's hemlock trees within the next decade. According to the study, researchers found "hemlock woolly adelgid infestation is rapidly impacting the carbon cycle in [hemlock] tree stands," and "adelgid-infested hemlock trees in the South are declining much faster than the reported 9-year decline of some infested hemlock trees in the Northeast."[17]

Closeup of bark

In a 2009 case study, entomologists from the U.S. Forest Service, Cornell University, and the University of Massachusetts-Amherst released 900 Laricobius nigrinus beetles into a stand of adelgid-infested hemlocks near Lansing, New York. L. nigrinus, which is native to the Pacific Northwest, naturally preys on the hemlock wooly adelgid. The particular site near Lansing was chosen because its hemlocks are only lightly infested with the woolly adelgid, and enough trees are found to sustain a long-term study. The site will be left untreated with pesticides for 10 years to study how well the L. nigrinus beetles become established; if the experiment proves successful, researchers expect the population will take two to three years to build to levels where they can be readily detected.[18]

Ecology

The tree can be found living in association with many forest mushrooms, such as Ramaria flavosaponaria.[19]

Paleoecology

The mid-Holocene decline of hemlock populations is a much-studied phenomenon.[20] From its foundation in the early Holocene (around 16,000 BP) in what is now the southeastern US, T. canadensis expanded rapidly and successfully into its potential range.[21] However, palynological analyses show the hemlock population experienced a pronounced decline approximately 5,500 BP that lasted for about 1,000 years. Continued research points to other, though less dramatic, dips in Holocene hemlock populations.[20][22] Pathogens, insects, and climatic change, and a combination of these, have all been proposed to explain these anomalies. The eastern hemlock increased again after the major decline, but did not recover its former place as a dominant species.

Exceptional trees

Due to its being a long-lived tree, several very large or otherwise impressive trees exist along the east coast of North America. One organization, the Eastern Native Tree Society (ENTS), has been particularly active in discovering and measuring these trees. In the southern Appalachians, many individuals reach 45 metres (148 ft) tall, and one tree has been measured in the Great Smoky Mountains National Park to 52.8 m (173 ft 3 in) tall, though this tree is now dead from hemlock woolly adelgids; the tallest now surviving, the "Noland Mountain tree", is 51.8 m (169 ft 11 in) tall.[16] Altogether, ENTS has confirmed four trees to heights of 51 m (167 ft) or more by climb and tape drop. In the Northeast, the tallest accurately measured tree is 44 m (144 ft). This tree, named the Seneca hemlock, grows in Cook Forest State Park, PA. Above 43°N latitude, the maximum height of the species is less, under 39 m (128 ft). In New England, ENTS has measured hemlocks to 42 m (138 ft), although trees above 39 m (128 ft) are extremely rare in New England. By 44°N, the maximum height is probably not more than 35 m (115 ft). Diameters of mature hemlocks range from 0.75–1.8 m (2 ft 6 in – 5 ft 11 in), with trees over 1.6 m (5 ft 3 in) in diameter being very rare. In New England, the maximum diameter is 1.4 m (4 ft 7 in).

Trunk volume is the third dimension to receive attention by ENTS. Many eastern hemlocks have been modeled to over 30 m3 (1,100 cu ft) trunk volume, and the largest has been calculated to be 44.8 m3 (1,580 cu ft),[16] making it the largest natural evergreen conifer in the eastern United States. The center of maximum size development for the species is the southern Appalachians, especially the Great Smoky Mountains.

Cultivation

Tsuga canadensis has long been a popular tree in cultivation. The tree's preference for partial shade and tolerance of full shade allows it to be planted in areas where other conifers would not easily grow. In addition, its very fine-textured foliage that droops to the ground, its pyramidal growth habit, and its ability to withstand hard pruning make it a desirable ornamental tree. In cultivation, it prefers sites that are slightly acidic to neutral with nutrient-rich and moist but well-drained soil. It is most often used as a specimen, for a screen, or in small group plantings, though it can also be trained as a dense formal hedge. It should not be used on roadsides where salt is used in winter, as its foliage is sensitive to salt spray. It is also poorly adapted as a windbreak tree, as wind exposure causes dieback in winter. It has several drawbacks, such as a fairly low tolerance of urban stress, intolerance for very wet or very dry soils, and susceptibility to attack by the hemlock woolly adelgid, though this is treatable.[23] Its tendency to shed needles rapidly after being cut down renders it unsuitable as a Christmas tree.

It was introduced to British gardens in 1736.[24] In the UK, it is encountered frequently in gardens both large and small, as well as some parks, and is most common in the eastern areas of the country. It is sometimes employed as a hedge, but is considered inferior for this usage compared to Tsuga heterophylla (western hemlock); it is not well adapted to the UK climate and as a consequence often has a poorly developed, forked and sinuous trunk there.[24][25] In Germany, it is the most frequently seen hemlock in cultivation, and is also used in forestry.[26]

Cultivars

The weeping shrub form T. canadensis 'Sargentii'

Over 300 cultivars have been selected for use, many of them being dwarf forms and shrubs. A partial list of popular cultivars includes:[23][27]

  • 'Beehive' – a very small dwarf shrub typically growing to 1 m (3 ft 3 in) high and 1.5 m wide, resembling a spreading beehive in form
  • 'Bennett' – a dwarf shrub reaching 1 m (3 ft 3 in) high and 1.5 m (4 ft 11 in) wide, with upper branchlets that first ascend and then arch upper, this selection prefers partial shade.
  • 'Cole's Prostrate' – a groundcover form that can also be used in bonsai as an alternative to the prostrate junipers, it slowly grows to only 30 cm (12 in) tall with a 1.3-metre (4.3 ft) spread, with the central stems eventually becoming visible. It also prefers partial shade.
  • 'Gentsch White' – a dwarf shrub growing to 1.3 m (4 ft 3 in) tall with an equal spread and new spring growth that turns creamy-white in autumn through winter, creating a dramatic contrast with the dark green old growth, it is easily scorched by the sun and requires partial shade. It is recommend to feather shear annually to keep it compact and create more tip growth.
  • 'Jeddeloh' – a dwarf shrub reaching to 1 m (3 ft 3 in) high and 1.5 m (4 ft 11 in) wide, showing a small concavity in the centre, it is an alternative to the bird's-nest spruce (Picea abies 'Nidiformis'). This cultivar has gained the Royal Horticultural Society's Award of Garden Merit.[28]
  • 'Pendula' – an upright weeping form whose height is dependent on how long it is staked, but is typically seen 0.6–1.5 m (2 ft 0 in – 4 ft 11 in) tall with a 1.5-metre (4.9 ft) spread. It has also won the AGM.[29]
  • 'Sargentii' – a popular large weeping shrub that grows to 3 m (9.8 ft) tall with a wide spread up to 6 m (20 ft), it features numerous pendulous branches and is most effectively employed near water, in rock gardens, or on embankments.

Uses

American pioneers made tea from the tree's leafy twigs and used its branches as brooms.[30] Tea can be made from the needles. The inner bark, which is best in winter and coming into spring, can be eaten raw or boiled; it can also be used to make flour.[31]

References

  1. ^ a b Farjon, A. (2013). "Tsuga canadensis". IUCN Red List of Threatened Species. 2013: e.T42431A2979676. doi:10.2305/IUCN.UK.2013-1.RLTS.T42431A2979676.en. Retrieved 11 November 2021.
  2. ^ "NatureServe Explorer 2.0". explorer.natureserve.org. Retrieved 12 April 2022.
  3. ^ USDA, NRCS (n.d.). "Tsuga canadensis". The PLANTS Database (plants.usda.gov). Greensboro, North Carolina: National Plant Data Team. Retrieved 12 December 2015.
  4. ^ BSBI List 2007 (xls). Botanical Society of Britain and Ireland. Archived from the original (xls) on 2015-06-26. Retrieved 2014-10-17.
  5. ^ a b c d e f g h Taylor, Ronald J. "Tsuga canadensis". In Flora of North America Editorial Committee (ed.). Flora of North America North of Mexico (FNA). New York and Oxford – via eFloras.org, Missouri Botanical Garden, St. Louis, MO & Harvard University Herbaria, Cambridge, MA.
  6. ^ Godman, R. M. "Eastern Hemlock". www.srs.fs.usda.gov. Retrieved 2021-12-13.
  7. ^ Gove, J.H.; Fairweather, S.E. (1988). "Tree-ring analysis of a 500-year old hemlock in central Pennsylvania". U.S. Forest Service General Technical Report NC-120. Vol. 1. pp. 483–489.
  8. ^ Blozan, Will (February 16, 2007). The Usis Hemlock Climb. Retrieved 2007-06-08.
  9. ^ Blozan, Will (December 18, 2006). The Laurel Branch Leviathan Climb. Retrieved 2007-06-08.
  10. ^ a b c d e Farjon, A. (1990). Pinaceae. Drawings and Descriptions of the Genera. Koeltz Scientific Books ISBN 3-87429-298-3.
  11. ^ Collingwood, C.H. and Warren D. Brush (Revised and Edited by Devereux Butcher). 1974. Knowing Your Trees. American Forestry Association. Washington, District of Columbia. 374 pp. ("EASTERN HEMLOCK", pp. 88-89.)
  12. ^ South, David B. (2016). "Eastern hemlock found in Macon County, Alabama".
  13. ^ Thompson, Robert S.; Anderson, Katherine H.; Bartlein, Patrick J. (1999). "Tsuga canadensis". Atlas of Relations Between Climatic Parameters and Distributions of Important Trees and Shrubs in North America (PDF). U.S. Geological Survey. Retrieved 2007-07-05.
  14. ^ a b Godman, R. M.; Lancaster, Kenneth (1990). "Tsuga canadensis". In Burns, Russell M.; Honkala, Barbara H. (eds.). Conifers. Silvics of North America. Washington, D.C.: United States Forest Service (USFS), United States Department of Agriculture (USDA). Vol. 1. Retrieved 2007-07-05 – via Southern Research Station.
  15. ^ McClure, M. S. (1987). "Biology and control of hemlock woolly adelgid" (PDF). Bulletin of the Connecticut Agricultural Experiment Station. 851: 1–9. Retrieved October 24, 2011.
  16. ^ a b c Earle, Christopher J., ed. (2018). "Tsuga canadensis". The Gymnosperm Database.
  17. ^ Hemlock Trees Dying Rapidly, Affecting Forest Carbon Cycle
  18. ^ Predator Beetle to Battle Hemlock Pest
  19. ^ Petersen, Ronald H. (November 1985). "Notes on Clavarioid Fungi. XX. New Taxa and Distributional Records in Clavulina and Ramaria". Mycologia. 77 (6): 903–919. doi:10.2307/3793302. ISSN 0027-5514. JSTOR 3793302. OCLC 7377077277.
  20. ^ a b Oswald, W. W.; Foster, D. R. (8 August 2011). "Middle-Holocene dynamics of Tsuga canadensis (eastern hemlock) in northern New England, USA" (PDF). The Holocene. 22 (1): 71–78. doi:10.1177/0959683611409774. S2CID 42106379. Retrieved 6 March 2013.
  21. ^ Delcourt, Hazel R.; Delcourt, Paul A. (1991). Quaternary Ecology: a Paleoecological Perspective (1st ed.). London: Chapman and Hall. pp. 43–44. ISBN 978-0-412-29790-8.
  22. ^ Zhao, Yan; Yu, Zicheng; Zhao, Cheng (23 April 2010). "Hemlock (Tsuga canadensis) declines at 9800 and 5300 cal. yr BP caused by Holocene climatic shifts in northeastern North America". The Holocene. 20 (6): 877–886. Bibcode:2010Holoc..20..877Z. doi:10.1177/0959683610365932. S2CID 220988296.
  23. ^ a b "Tsuga canadensis". UConn Plant Database. University of Connecticut. Retrieved 19 August 2013.
  24. ^ a b Mitchell, A. F. (1974). A Field Guide to the Trees of Britain and Northern Europe. Collins ISBN 0-00-212035-6
  25. ^ Mitchell, A. F. (1972). Conifers in the British Isles. Forestry Commission Booklet 33.
  26. ^ (in German) Schmeil, O., Fitschen, J., & Seybold, S. (2006). Flora von Deutschland 93. Auflage, p. 424. Quelle & Meyer Verlag, Wiebelsheim. ISBN 3-494-01413-2.
  27. ^ Welch, H., & Haddow, G. (1993). The World Checklist of Conifers. Landsman's. ISBN 0-900513-09-8.
  28. ^ "Tsuga canadensis 'Jeddeloh'". Royal Horticultural Society. Retrieved 13 March 2021.
  29. ^ "Tsuga canadensis 'Pendula'". RHS. Retrieved 5 March 2021.
  30. ^ Little, Elbert L. (1980). The Audubon Society Field Guide to North American Trees: Eastern Region. New York: Knopf. p. 300. ISBN 0-394-50760-6.
  31. ^ Elias, Thomas S.; Dykeman, Peter A. (2009) [1982]. Edible Wild Plants: A North American Field Guide to Over 200 Natural Foods. New York: Sterling. p. 122. ISBN 978-1-4027-6715-9. OCLC 244766414.

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Tsuga canadensis: Brief Summary

provided by wikipedia EN
An Eastern Hemlock branch at the Kortright Centre for Conservation.

Tsuga canadensis, also known as eastern hemlock, eastern hemlock-spruce, or Canadian hemlock, and in the French-speaking regions of Canada as pruche du Canada, is a coniferous tree native to eastern North America. It is the state tree of Pennsylvania. Eastern hemlocks are widespread throughout much of the Great Lakes region, the Appalachian Mountains, the Northeastern United States, and Maritime Canada. They have been introduced in the United Kingdom and mainland Europe, where they are used as ornamental trees.

Eastern hemlock populations in North America are threatened in much of their range by the spread of the invasive Hemlock woolly adelgid, which infests and eventually kills trees. Declines in population from hemlock wooly adelgid infestation have led to Tsuga canadensis being listed as Near Threatened on the IUCN Red List.

Eastern hemlocks are long lived trees, with many examples living for more than 500 years. They can grow to heights of more than 30 metres (100 ft), and are tolerant of shade, moist soil, and slopes. Hemlock wood is used in construction, and for railroad ties. Historically its bark was an important source of tannin for the leather tanning industry. Eastern hemlocks are popular as ornamental trees, thanks to their tolerance of a wide variety of soil and light conditions, as well as their characteristic drooping branches.

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