Temperate deciduous (mesophytic) forests  Distribution  Climate  Soils  Forest types and structure  Plant ecophysiology  Fauna  History (Tertiary.

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Presentation transcript:

Temperate deciduous (mesophytic) forests  Distribution  Climate  Soils  Forest types and structure  Plant ecophysiology  Fauna  History (Tertiary - PD)  Disturbance  Forest clearance  Succession

Global distribution of the biome Deciduous forests

North American distribution of the TDF and representative climate stations Boston Atlanta Little Rock Madison

Climate - monthly temperatures

Climate - precipitation regimes

Soil types of the temperate deciduous forest Alfisols Ultisols (Inceptisols)

Soil profiles and soil-forming processes Cool temperate areas: Alfisols/Luvisols/Brown Earths Warm temperate areas: Ultisols

Soil formation Alfisols (etc.) - the broadleaf deciduous trees exert a greater demand on soil nutrient resources than the conifers of the boreal forest, and their leaves are more base-rich. Incorporation of litter into the soil by earthworms produces humus-rich A and B horizons. Iron and aluminium are not mobilized, but clay particles, which tend to be dispersed in base-rich soils, are transported down to form a clay-rich B horizon. Ultisols replace alfisols in warm temperate areas as a result of more advanced weathering. Generally less fertile; often degraded in the southeastern USA by plantation agriculture.

What controls the distribution of the dominant tree species of the TDF? Clockwise, from top left: Acer saccharum, Tilia americana, Ostrya virginiana, Ulmus americana, Ulmus rubra, and Quercus rubra

Temperate forest trees: similar western limits = similar drought intolerance? American beech red oak red maple (plus white oak, black oak, 2 hickories.... )

Airmass climatology - biome boundaries

D = R / (L x P) where D = dryness ratio; R = mean ann. net radiation; P = mean ann. precipitation; L = latent heat of vaporization of water Budyko-Lettau dryness ratio

The forest- prairie boundary Budyko suggested that the forest - grassland boundary in the midwest corresponds with a dryness ratio of (=dotted line) Budyko dryness ratio values, N. America Hare (1980) Atmos.-Ocean 18,

Tree species diversity Is reduced diversity to northwest a result of the harsher climate?

Temperate forest trees: common northern limits = similar limiting temperatures? American beech red oak red maple (plus white oak, black oak, 2 hickories.... )

Airmass climatology - biome boundaries

Thermal limits and optima

Cold injury

Probability of temperatures falling below -40°C A = common B = rare C = never American beech

Winter-summer phases

Daily irradiance*: Liriodendron stand, Tennessee Photosynthetic activity Trees Vernal ephemerals Summer herbs Evergreens (sun plants) (shade plants) * values are langleys/day

Shade tolerance of N. American TDF trees Intolerant Intermediate Tolerant Very Tolerant yellow poplar (Liriodendron tulipifera) - pioneer black locust (Robinia pseudoacacia) - pioneer black cherry (Prunus serotina) black walnut (Juglans nigra) white ash (Fraxinus americana) red and white oak (Quercus rubra, Q. alba) hickories (Carya spp.) sweet birch (Betula lenta) - pioneer basswood (Tilia americana) red maple (Acer rubra) sugar maple (Acer saccharum) American beech (Fagus grandifolia) eastern hemlock (Tsuga canadensis)

Periodicity of acorn production (note variable behaviour within and between oaks) Black oakWhite oak “never” every year for five years

Old-field succession (Northern hardwoods) Pioneer phase - 20 yr old stand of pin cherry (Prunus sp.) in S. Ontario. Bird dispersal.

Fire / old-field succession (mixed forests of the southeast) Oak - hickory (tulip tree, magnolia, dogwood) Pine (shortleaf/longleaf) weedy herbs Year 50 5

Modern forest fauna (N. America) Characteristic animals are now either herbivores (predominantly seed eaters) or omnivores. Herbivores: white-tailed deer, gray squirrel, chipmunk, blue jay (passenger pigeon - extinct). Omnivores: raccoon, opossum, skunk, black bear. Carnivores: (wolf, cougar, bobcat - all largely eliminated by hunting and habitat destruction; replaced by coyote)

Many northern temperate forest tree genera are widespread Quercus (oak) Acer (maple) Fagus (beech) Castanea (chestnut) Carya (hickory) Ulmus (elm) Tilia (basswood/linden) Juglans (walnut) Liquidambar (sweet gum) Liriodendron (yellow poplar) E N AmEuropeE Asia XXX XFX XXX XFX X = extant; F = fossil

Biomes of the early Tertiary (~60 Ma)

Eureka Sound formation: Ellesmere Is*. Gymnosperms: Cedrus, Picea, Pinus, Tsuga Angiosperms: Acer, Betula, Carya, Corylus, Castanea, Fagus, Quercus Fauna: turtles, alligators, boid snakes, salamanders, tortoises *

Tertiary cooling and the temperate mesophytic forest southward retreat expansion fragmentation

Eurasian - North American temperate forest divergence (from genetic evidence) Xiang et al., Mol. Phylogenet. and Evol. 15, Liriodendron chinense Liriodendron tulipifera (Magnoliaceae)

Pliocene fragmentation

Full-glacial refuges (R) and Holocene migrations R? White pine E. hemlock Oaks Elms

(=a x b) (a) (b) (c) (=a x c)

Rapid post-glacial migration: are seed-caching birds responsible? What role do they play in long-distance dispersal at present? Fagus grandiflora Quercus macrocarpa blue jay passenger pigeon

Postglacial fossil finds: passenger pigeon (dots) and blue jay (triangles )

Why is the European TDF depauperate? Quercus (oak) Acer (maple) Fagus (beech) Castanea (chestnut) Carya (hickory) Ulmus (elm) Tilia (basswood) Juglans (walnut) Liquidambar (sweet gum) Nyssa (sour gum) E N AmEuropeE Asia XXX XFX XXX XFX X = extant; F = fossil

Late Quaternary dynamics (Europe) yrs BP present

Recent species fluctuations: pest- pathogen effects on species dynamics (+ Dutch elm) Chestnut blight ( ) (Endothia parasitica) Hemlock looper? (Lamdina fiscellaria) What effects do these die-outs have on the success of competitors?

Plant community structure as a function of topography and elevation in the Great Smoky Mountains

Plant community structure as a function of topography, substrate and disturbance frequency in Michigan

Disturbance and ecological succession Fire Wind Anthropogenic (forest clearance) Examine the roles of:

Natural disturbance: lightning-strike fires

Natural fire recurrence “from 1955 to 1994 only 5 years had records of lightning-set fire, with an average of 7 years between fires. Lightning strikes occurred on ridge tops and along xeric upper hillslopes (and) did not spread into lower sheltered coves or stream valleys.” Delcourt, H.R. & Delcourt, P.A Conservation Biol., 11, p

Natural disturbance: hurricane windthrow Erin (160) Dean (70) Alison (120)Jerry (65) Paths of tropical storms in 1995, and their maximum wind speed in km/h.

Natural disturbance: tornado windthrow Paths of F3-F5 tornadoes in USA: Graphic:

Windstorm disturbance: local and regional Tornado path (above: satellite image) and forest damage (below) in Menominee Reservation, Wisconsin, June 2007 Path almos t 1 km wide Great Storm of 1987: 15 million trees blown over in southern Britain 90 knots = 170 km/h

Anthropogenic disturbance: agricultural clearance Intensive cultivation Extensive cultivation Woodland landscape (local disturbance) Woodland landscape (little disturbance) W Europe China N America Archaic (hunting, fire, nuts) Woodland (shifting cultivation) Mississippian European

Anthropogenic disturbance and forest remnants (Europe) Forest patches on steeper slopes and distant from villages

Clearing the forest primeval: northern England Roman Mesolithic (2000 BP) (8000 BP) Medieval Late Bronze Age (6000 BP) (4500 BP)

Forest management: coppicing and charcoal production ~10,000 poles/acre baskets, farm implements, barrels, soap (from ash) Dried poles

Forest management: animal husbandry Pannage Right to feed pigs in the forest acorns, beechmast, sweet chestnuts

Or was the primeval forest “open”? Vera (2000) argues that the early forest was “open”, primarily based on these lines of evidence:  palynology (lots of hazel pollen)  abundance of oak (mid- successional species)  presence of large herbivores (aurochs, bison, horses, etc.)  Classical and medieval descriptions of “forestis”

Late Quaternary forest fauna (Europe)

The Vera hypothesis Should large grazers be re-introduced as a tool of forest management? Graphic: Mitchell, F.J.G J. Ecol., 93,

Testing the Vera hypothesis: distribution of European herbivores in early Holocene SpeciesNW EuropeBritainIreland Wild boar (Sus scrofa) yes Red deer (Cervus elaphus) yes Roe deer (Capreolus capreolus) yes no Elk (Alces alces) yes no Reindeer (Rangifer tarandus) yes no Horse (Equus caballus s.l.) yes no Aurochs (Bos primigenius) yes no Beaver (Castor fibre) yes no Bison (Bison spp.) yesno Fallow deer (Dama dama) yesno Mitchell, F.J.G J. Ecol., 93,

Testing the Vera hypothesis: pollen in small forest hollows Percent (mean ±1  ) tree pollen in modern “forest-parkland” Ireland S. Sweden Mitchell, F.J.G J. Ecol., 93,

Fire regimes? Clark et al., J. Ecol., 97, Data from southwestern Germany * *”Atlantic” in the Blytt-Sernander sequence Fires in mid-Holocene at ~250-yr intervals; successional sequence: Corylus avellana Ulmus (elm) (hazel) >> Quercus (oak) >> >> Fagus (beech) Fraxinus excelsior Tilia (lime) (ash)

If oak is a mid-successional tree, and natural fire is rare, why are oaks a dominant species in the TDF of the eastern USA? Source: Copenheaver, C.A., et al., Northeastern Naturalist, 13, Tree and sapling diameters, Watertower stand, Fishburn Forest, VA Tree and sapling diameters, Radio Tower stand, Fishburn Forest, VA

Forest constancy because of anthropogenic fire? Delcourt, H.R. & Delcourt, P.A Conservation Biol., 11, p oak 4000 BP chestnut Euro- settlemen t Macon Co., N. Carolina

Indians as ecological agents in the forests of northeastern America In 1669 Galinée visited a Seneca village (in modern NY State). The village was in an agricultural clearing about 6km wide; Village sites were abandoned every years as the soil became exhausted Forests near villages were burned each spring and fall to remove undergrowth and improve grazing for deer and elk. An Algonkian village Abstracted from: Day, G.M Ecology, 34,