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Part II: The Macro Approach: Managing Forest Landscapes

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Title: Part II: The Macro Approach: Managing Forest Landscapes


1
Part II The Macro ApproachManaging Forest
Landscapes
  • Species Composition
  • Age Structure
  • Spatial Heterogeneity
  • Edges
  • Islands Fragments
  • Shores

2
Species CompositionPart 4
  • Fundamentals
  • Understanding trees species
  • Distribution across landscape
  • Environmental Factors Affecting Forest
    Composition
  • Intrinsic
  • Climate Soil
  • Extrinsic
  • Affected by succession
  • Presence of competitors
  • Changes quickly
  • http//www.extension.iastate.edu/Publications/SUL1
    .pdf
  • Understanding the Effects of Flooding on Trees
  • Ecosystem Relations Straightforward
  • Oak-hickory on uplands sugar maple on
    bottomlands

3
Species CompositionPart 4
  • Tree Species Wildlife
  • Trees food, cover, shelter, substrate
  • Some relationships specific
  • Jack pine have spruce grouse
  • Most relationships loose between tree species and
    organisms
  • Tree architecture may be more important than food
    abundance
  • Bird/mammal movement
  • CorrelationBird species diversity and number of
    tree and shrub species

4
Species CompositionPart 4
  • Conifers Deciduous Trees
  • Deciduous trees have richer biota
  • Not distasteful
  • Evolved at time animals evolved
  • Seed dispersal, pollination, herbivory
  • More structural diversity
  • Conifers
  • Distasteful
  • Needles unpalatable to decomposers as well
  • Do provide winter cover

5
Species CompositionPart 4
  • Exotic Trees
  • Displace natives
  • Impacts wildlife, especially herbivores
  • Examples of exotics
  • Scots pine
  • Fraser fir
  • Norway spruce
  • http//www.extension.iastate.edu/Publications/PM19
    81.pdf
  • Woodland Invasive Species

6
Species CompositionPart 4
  • Monocultures
  • Single dominant species
  • Moderately common
  • Single species only
  • Uncommon
  • Characterize planted plantations by humans
  • Pests and pathogens
  • Disease prone
  • Simplicity makes easier to manage
  • Economic justification

7
Species CompositionPart 4
  • Longleaf Pine
  • Video

8
Species CompositionPart 4
  • Conclusion
  • Choose native species
  • Avoid exotics
  • Plant two or more species
  • Strive for diversity
  • Conifer and deciduous tree
  • Avoid increasing extent of conifers substantially

9
Pines
10
Pinus strobus
  • White Pine
  • Needles in bundles of five
  • 2-4 inches long.

11
Larix sp.
  • Larches or Tamaracks
  • Many needles (7-24) per fasticle
  • occurring on spur-like shoots
  • needles fall in autumn.

12
Pinus nigra
  • Austrian Pine
  • Needles in bundles of two,
  • 4-6 inches long needles are thick and stiff,
  • folding when bent.

13
Pinus resinosa
  • Red Pine
  • Needles in bundles of two,
  • 4-6 inches long.
  • Needles are thin and brittle
  • snap when bent.

14
Pinus ponderosa
  • Ponderosa Pine
  • Needles in bundles of twos and threes,
  • 5-8 inches in length.

15
Pinus sysvestris
  • Scotch Pine
  • Needles in bundles of two,
  • 11/2-3 inches long and twisted
  • bark on older trees is orange and scaly.

16
Pinus banksiana
  • Jack Pine
  • Needles in bundles of two,
  • 3/4-11/2 inches long, twisted
  • cone tips curve toward the branch tips.

17
Conifer ID
  • http//www.extension.iastate.edu/Publications/PM13
    83.pdf

18
Age Structure
  • Chapter 5

19
Age StructurePart 5
  • Iowas Woodlands
  • http//www.extension.iastate.edu/Publications/IAN2
    02.pdf
  • Perspective
  • Forest age since last disturbance
  • Fire, glacier, logging
  • Succession
  • Plants influenced by microclimate and competition
  • Animals influenced by plant community
  • Managing Forests Managing Diversity
  • http//www.extension.iastate.edu/Publications/PM13
    51I.pdf
  • Managing Patterns of Succession
  • Determine age Structure of Landscape
  • Iowas Trees

20
Age StructurePart 5
  • Diversity Succession
  • Managing forests for diversity involves patterns
    of succession
  • Some successional stages have more species than
    others
  • Each stage has a different set of species
  • Greatest Diversity
  • Climax
  • Immediately after disturbance
  • Forest landscape with many successional stages
    will be more diverse

21
Age StructurePart 5
  • Balancing Age Classes
  • Failure
  • Pest and pathogen outbreaks
  • Temporal bottlenecks
  • Species of wildlife requiring specific age stands
    of a forest
  • Diagrams

22
Age StructurePart 5
  • Old Forests
  • Trees ready for harvest
  • Growth rate .0022 cubic meters in 80th year
  • Averaged .0023 other 79 years

23
Age StructurePart 5
  • Old Forests Defined
  • Environmentalist Definition
  • Primeval
  • Ancient
  • Wilderness
  • Virgin
  • Pristine
  • Foresters Definition
  • Overmature
  • Decadent
  • senescent
  • Scientist Definition
  • Old growth

24
Age StructurePart 5
  • Age Criteria
  • Forest age where species composition is stable
  • Forest age where average net growth near zero
  • Forest significantly older than average interval
    between natural disturbances severe enough to
    lead to succession
  • Dominant trees reached life expectancy
  • Iowas oak trees
  • Iowas Oaks RG701
  • Forests current annual growth rate declined
    below the lifetime average annual growth rate

25
Age StructurePart 5
  • Disturbance Criteria
  • Forest extensively or intensively cut?
  • Forest converted to another ecosystem?

26
Age StructurePart 5
  • Importance of Old Forests
  • Adequate Number
  • Adequate Area
  • Represent one portion of successional sequence
  • Most biologically diverse portion of sequence
  • Species dependent on old forest
  • Example Douglas fir wester hemlock stands of
    Pacific northwest
  • Northern Spotted owl
  • Hammonds flycathers
  • Red tree voles
  • Lichens
  • Saprophytic plants
  • Synergism More than a sum of their parts

27
Age StructurePart 5
  • How Much is Needed?
  • Controversial example
  • Pacific Northwest virgin old growth forests
  • Spatial requirements
  • Home ranges
  • Minimum area needed

28
Age StructurePart 5
  • Managing for Old Forest Species
  • Provide maximum habitat as feasible
  • Disturbances
  • Human and natural
  • Air pollution
  • Lightning
  • Forest Management
  • Lengthen rotations
  • Allow some stands to reach 100 years (normally
    cut _at_ 80 years)
  • Allow some to reach 320 years
  • Deer needs
  • Dense canopy intercepts snow

29
Figure 5-12
30
Age StructurePart 5
  • Spotted Owl
  • Pacific Northwest
  • Large tracts 1,7000 ha old growth conifer forests
  • Economically worth 10,000 per ha
  • Northern Spotted Owl
  • Estimated population 4,000-6,000
  • Home range 1,700 ha in WA to 800 ha in CA
  • Old forests virgin stands gt200 years
  • Thick canopy may shleter primary prey
  • Northern flying squirrels wood rats
  • Ill equipped to resist or recover from
    catastrophes
  • Breed at 3 years
  • .49 fledgings/year
  • Juvenile Survivorship 11
  • Adult survivorship 80-96
  • Value of spotted owl as indicator of condition of
    old growth forest

31
Age StructurePart 5
  • Conclusion
  • Various plant and animal species associated with
    different stages of succession
  • Balancing age structure of forest accomplishes
    two objectives
  • Sustained yield of forest products
  • Provide diverse wildlife habitat
  • Forest management can enhance biological
    diversity
  • Forests become economically mature long before
    becoming biologically mature
  • Important to protect and maintain a reasonable
    area of old forest to maintain a reasonable area
    of old forest to maintain populations of species
    that are associated with this habitat and
    community as whole

32
Spatial Heterogeneity
  • Chapter 6

33
Spatial HeterogeneityPart 6
  • Introduction
  • Organisms need habitat
  • Size of the organism influences size of the
    habitat
  • Bears need more room than rabbits
  • Predators have to cover large areas to find
    enough herbivores to eat
  • Organisms vary in extent to which they need a
    diverse environment
  • Habitat specialists
  • Some Need uniform environment
  • Others Need diverse environment
  • Woodcock
  • Needs forest openings to roost display, alder
    swamps to forage 15-30 year deciduous stands for
    nesting and brood rearing
  • Diversity of forest depends on scale at which it
    is viewed by individual species
  • Some species can live in a variety of habitats
    some require a diverse habitat and some require a
    fairly uniform habitat

34
Spatial HeterogeneityPart 6
  • Natural Disturbance Harvesting Systems
  • Inherent spatial heterogeneity in forests
  • Soil, topography, patterns of disburbance
  • Small scale toppling of tree
  • Shade tolerant trees Uneven aged
  • Large scale lightning fires
  • Average disturbance rate 1 per year
  • One age class so even-aged
  • Shade tolerant and shade interolerant
  • Harvest systems
  • Clearcutting even aged management harvest al
    trees
  • Selection cutting small portion of trees
    removed uneven aged
  • Weeding or grown to maturity
  • Patch cut minimum size .1 hectare
  • Group selection cutting clumps of trees to be
    removed are identified
  • Shelterwood cutting seed source trees left and
    shelter trees left

35
Spatial HeterogeneityPart 6
  • Managing for Spatial Heterogeneity
  • Selection cutting tool for maintaining diversity
    on small scale
  • Assures trees of many different ages within each
    stand
  • Forest diversity on landscape scale
  • Selection cutting
  • Patch cutting
  • Clear cutting
  • Iowas Woodland Management Understanding Trees
    Woodlands

36
Spatial HeterogeneityPart 6
  • Model for Spatial Heterogeneity
  • Fragmented Forest (Larry Harris)
  • Divised ideal frequency distribution for
    different size fragmentsof old-growth forests
  • More small stands than large ones
  • More populations of small organisms than large
    organisms
  • Smaller species have smaller home ranges
  • Precedents of natural landscapes
  • Watersheds and stream lengths
  • Tributaries vs. continent draining rivers
  • Model
  • 10,000 patches of .01 ha 1,000 ha
  • 10,000 patches of .1 ha 1,000ha
  • 1,000 patches of 1 ha
  • 100 of 10 ha
  • 10 of 100 ha

37
  • Model Rationale
  • Harvest forests at a range of different scales
  • Allocate approximately equal areas to different
    points along the continuum from small scale to
    large scale
  • Large species more likely to be threatened with
    extinction

38
Spatial HeterogeneityPart 6
  • How big should clearcuts be?
  • Size of management unit
  • The more land in management unit, larger the
    clearcuts can be
  • Coordinate forest management over etremely large
    areas
  • Habitat requirement of animals
  • Large animals have huge home ranges
  • Aesthetics
  • Slash of clearcuts people find offfensive
  • Straight edges offensive dont seem natural
  • Soil erosion and nutrient loss
  • Nutrition depletion from removal of trees
    slash greater loss larger cuts
  • Natural disturbances as models
  • Cuts not to exceed size of natural disasters
  • Controversial clearcuts and compromises
  • Visual impact
  • Negative effective impact on wildlife

39
Edges
  • Part 7

40
EdgesPart 7
  • Edge Effect
  • Aldo Leopold Game Management
  • Create more edge
  • Cardinal rule of game management
  • Diversity and abundance of wildlife greatest near
    edge
  • Edge effect
  • No longer accepted as universal rule of game
    management
  • Edges
  • Where two ecosystems come together
  • Ecotones
  • Transition zone from one set of environmental
    conditions to another
  • May be based on inherent feature of a site
    inherent edges
  • Rise in topography
  • Altitude
  • Permanent or temporary

41
EdgesPart 7
  • Edge Effect
  • Game animals embrace edges
  • Tend to be large and shy
  • Need food of open, younger area
  • Need cover of older ecosystem
  • Second group of plants and animals is preferred
    habitat
  • Unique conditions of habitat itself
  • Many species living in ecotone only secondarily
    edge species
  • Tolerate both ecosystems
  • Large number of species use edge for variety of
    reasons
  • Some species find it preferred habitat

42
EdgesPart 7
  • Other Side of Edge Effect
  • Higher rates of nest predation
  • Cowbirds lays its eggs in other birds nests
  • 67
  • Reductions in regeneration of many trees, shrubs,
    and herbaceous plants
  • Species shun edges favor forest interiors
  • Invasive species favor edges

43
EdgesPart 7
  • Creating Edges Through Forest Management
  • Edges Geometry
  • The more a shape diverges from a circle
  • The greater edge is created
  • The size of a stand affects edge on relative
    basis
  • Linear distances increase as additive function
  • Areas increase as square
  • Dissecting into many small stands creates more
    edge

44
EdgesPart 7
  • Coverts, Interspersion, Contrast
  • Leopold 1933
  • Optimal bobwhite habitat
  • Forest, brushland, grassland and cultivation
  • Three or more habitats adjoining must be even
    better
  • Coverts
  • Interspersion
  • Dispersion
  • Juxtaposition
  • All describe them being next to each other

45
EdgesPart 7
  • Summary
  • Edges (ecotones) support diversity of wildlife
    species
  • Forest managers have control over amount of edge
  • Small stands have more edge than larger edge
  • Irregular shaped stands have more edge
  • Significant negative side effects
  • Species avoid edges
  • High rates of predation
  • Brood parasitism

46
Islands Fragments
  • Part 8

47
Islands FragmentsPart 8
  • Introduction
  • Islands of forest habitat
  • Island biogeography
  • The Fragmented Forest (Larry Harris)
  • Forest harvesting can affect biological diversity
    by leaving stands as isolated habitat habitat
    islands

48
Islands FragmentsPart 8
  • Island Biogeograhy
  • Island Size
  • Small islands have fewer species than larger
    islands
  • As island size increases, the diversity of the
    physical environment increases
  • In a large area there are more likely to be
    uncommon species that ive at low population
    densities as well as common species
  • Small islands support small populations and small
    populations are more likely to go extinct
  • Genetic inbreeding
  • Random fluctuations in sex and age structure of
    the population
  • Changes in the environment
  • Catastrophic events
  • Flooding
  • Fires
  • Hurricanes
  • Causing local extinction

49
Islands FragmentsPart 8
  • Island Isolation
  • More isolated an island, few species it will
    support
  • Land bridge islands
  • Have fairly complete biota
  • Species gradually dwindles
  • Prone to extinction
  • Oceanic Islands
  • Begin with no terrestrial plants or animals
  • Over time gradually colonized by various species

50
Islands FragmentsPart 8
  • Symbiosis on Islands
  • Many species develop tight, symbiotic
    relationships
  • Relative scarcity of large, showy flowers on
    islands
  • Lack of butterflies and bees
  • Plants without specialized pollinators by using
    generalist pollinators

51
Islands FragmentsPart 8
  • Islands in the Landscape
  • Human dominated landscapes insulate caves,
    mountaintops and isolated patched of prairies and
    forests
  • Conversion of prairie and forest into
    agricultural ecosystems
  • Differences between islands and forest fragments
  • Water and open land two different barriers
  • Terrestrial animals isolated most by water
  • Aquatic animals isolated most by land
  • Ask isolated from WHAT?
  • Scope and intensity of interactions between
    members of a forest fragment community and
    members of the surrounding terrestrial community
    is likely much greater than degree of interaction
    between island and aquatic communities

52
Islands FragmentsPart 8
  • Birds Forest Fragments
  • Bird diversity-forest area relationship
  • Long distance migratory birds tend to produce
    only one small clutch of eggs per year, often
    laid in open nest close to ground
  • Makes vulnerable to nest predators
  • Nest predators and parasites are more effective
    near edges and in small fragments composed
    primarily of edge habitat
  • Late arrival of long distance migrants gives less
    opportunity for renesting
  • Some species thrive in small forest fragments
  • Others seldom found in small forests

53
Islands FragmentsPart 8
  • Nature Reserves as Islands
  • Design features that could help maintain species
    diversity
  • Large reserve
  • Single large vs. several small
  • If several small only choice, group closely
    together
  • Arrange in cluster fashion
  • Connect reserves with corridors to make dispersal
    easier
  • Make reserves circular as possible
  • SLOSS Debate (single large vs. several small)
  • Minimum viable population of large, wide ranging
    animals
  • Catastrophes argue against single large reserve
  • Sometimes two species dont coexist because they
    are competitors
  • Practical considerations
  • Harder to find large tracts of relatively
    undisturbed land

54
Islands FragmentsPart 8
  • Corridors
  • Link network of patches of forest
  • Long narrow habitat bridges
  • Effectiveness of corridors
  • depends on organism
  • Type of movement
  • Type of corridor
  • Iowas corridors
  • Waterways
  • Shorelands have many ecological values
  • Maintain wide bands of vegetation near shores

55
Islands FragmentsPart 8
  • Forest management Forest Fragmentation
  • Forestry Nature Reserves
  • Collaborate with other resource managers
  • Sensitive low impact techniques
  • Without compromising wildlife habitat

56
Islands FragmentsPart 8
  • Fragmentation in a Forested Landscape
  • Negative effects of forest fragments in ag
    regions
  • Large decrease in regions total area of forest
  • 1960 25 of earths surface
  • 2000 20
  • 2020 14
  • Douglas fir forests 30 year study in California
  • Amphibians, reptiles, birds
  • Edge and early successional species present
  • Interior species avoid these fragments
  • Nonmigratory species nesting in cavities
    declinging in populations
  • Potential fragmentation issues
  • Higher nest predation
  • Small mammals reluctant to cross 3m unused
    roadway
  • Regional extinction for some species

57
Islands FragmentsPart 8
  • Fragments Edges
  • Multiple use model (MUM)
  • Core
  • Undisturbed forest
  • Buffer zone
  • Inner buffer zone of dispersed recreation and
    selection and loging
  • Outer buffer zone
  • Variety of buffer zone and forestry activities
    and limited agriculture
  • Choices
  • game vs. nongame
  • Edge vs. interior species
  • Rare vs. common species

58
Islands FragmentsPart 8
  • Summary
  • Isolated patches of forest
  • Low habitat diversity
  • High rates of local extinction
  • Absence of species that live at low population
    densities
  • Deleterious seffects associated with edges
  • Avoid future fragmentation
  • Subject forest fragments to less disruptive forms
    of management
  • Manage extensively forested landscapes on variety
    of scales
  • Some most vulnerable species require extensive
    tracts of habitat

59
Shores
  • Part 9

60
ShoresPart 9
  • Introduction
  • Interface between aquatic and terrestrial
    habitats
  • Great importance
  • Shores home to unique biota
  • Special ecological processes
  • Timber management in riparian forests
  • Grasslands ribbon of trees marks watercourse
  • Forest streams come in different orders of
    classifications
  • Tributaries first order Mississippi tenth order
  • Parameters for riparian zone
  • Hydrologic
  • Climatic
  • Biological
  • Periodically inundated by high water

61
ShoresPart 9
  • Importance of Riparian Ecosystems
  • Aquatic Perspective
  • Steams not tremendously productive
  • Lack of organic matter
  • Invertebrate decomposers
  • Large logs stabilize dynamic equilibium
    deposition/erosion
  • Beaver dams
  • Forest stream biota
  • Narrow range of temperature
  • Forest canopy shades water
  • Holds more dissolved oxygen

62
ShoresPart 9
  • Terrestrial Perspective

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