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What is a “forest”?
Woody plats (trees, shrubs) are dominant vegetation
however, usually distinct from woodland
Often associated with precipitation
Components of forest management
Trees (species) define ecology
species describe “forest type”
Ecosystem structure
herbivores, predators, detritivores
Soil biota
Ecosystem function
productivity, energy sequestration, nutrient flow
Plant-soil feedback
brown food web important component of forest management
tree decomposition
primary and secondary cavity nesters
vertical structure important component of forest management
ground, shrub, midstory, canopy layers
species occupy different layers
scale is important component of habitat management
vegetation long-lived; long term management strategies necessary
age structure: even or uneven aged forests
forest succession component of forest management
stand initiation phase
stem exclusion phase
understory reinitiation phase
old growth phase
even-aged regeneration
removal of many trees, all same age class
clearcuts
seed-tree cuts
shelterwood cuts
single age-class dominates community
long regeneration period
early colonizers shade intolerant
even-aged regeneration: clearcuts
most common management; 2/3 of timber harvest
early successional habitat persists 5-20 years post cut
irreparable damage to understory
even-aged regeneration: clearcuts effects on wildlife
small clearcuts: (<10 ha provide habitat for edge species)
generalists, invasive species, early successional species
dense brush, understory cover
larger clearcuts provide habitat for some early successional birds
can promote shade intolerant oaks and shortleaf pines
what factors are important for management of clearcuts
size of clearcut
age of stands/time since clearcut
isolation of clearcut/heterogeneity
plant (species) composition
environmental characteristics
even-aged regeneration: thinning
killing or removal of trees to promote a certain density or structure
promotes space for trees to grow, reduce competition
precommercial
commercial
precommercial thinning
done prior to tree maturity, reduces cost of management
promotes growth of remaining trees
prolongs early successional communities and understory diversity
commercial thinning
select trees harvested throughout management to offset costs
even-aged regeneration: seed tree cuts
small group of trees (~5-10/ha) retained
benefits?
refuge for wildlife, plant species
birds facilitate regeneration
consequences?
reduced population diversity
susceptibility to disease, invasion
even-aged regeneration: shelterwood cuts
~10 year rotation:
preparatory cut
establishment cut
removal cut
retain trees to shelter regenerating trees
encourage shade-tolerant species
uneven aged management
fewer trees removed, variable age classes (~3)
cutting cycles (15-30 yrs NA)
promotes age class retention
shorter regeneration time
shade-tolerant species more likely
small scale management
horizontal structure management
line between clearcut and large-scale group tree removal vague
uneven aged management (horizontal structure management)
species vary in tolerance to shade for growth and development
single tree removal
group tree removal
what is the best approach for management? (forest)
goals of land use (timber production) define the approach
harvest (yield) important, but so is regeneration
depends on landscape characteristics
dominant plant type/species, soil, hydrology, etc
target species defines management
edge species vs interior species
sensitive/rare species, threatened/endangered species
are there additional patches of habitat available?
cavities and cavity nesting
primary cavity nesters/excavators
secondary cavity nesters
primary cavity nesters/excavators
excavate cavities of soft or rotting wood
may include living or dead plant tissue
occupancy depends on:
availability of food items (wood-boring prey)
competition
secondary cavity nesters
use cavities in trees that the animals themselves do not produce
obligate cavity nesters
opportunistic cavity nesters
obligate cavity nesters
require cavities to breed, incubate, and rear young
opportunistic cavity nesters
will use cavities only if available
retaining snags
how much cavities and usable positions animals have in order to be primary or secondary nester
S=DCX
S-suitable snag density (# snags/n ha)
D-density (max # nesting pairs/n ha)
C-# cavities excavated per pair/yr
X-# used + unused snags/n ha
estimate should support max # of pairs of a primary cavity nester
rotting logs and woody debris
decomposition rates depend on Decay Rate Constant
Dt+D0e-kt
where:
D=wood density (# trees/ha)
t=time (years)
e=natural log
k=decay rate constant (species-specific)
woodpeckers (picidae)
important habitat characteristics:
dead wood for cavity nesting
diverse vertical structure
plant composition/species
dead wood snags
virginia mixed-oak forests underwent clear-cut
improved habitat quality first year, but not second year
1st yr- increased litter and debris (arthropods)
2nd yr-fewer cavities
plethodon salamanders (caudata, plethodontidae)
important habitat characteristics
water bodies (larva), soil moisture (adults)
canopy cover
plant composition (understory)
litter composition/abundance
arthropod availability (prey)
clearcut oak-hickory forests in north carolina
pennsylvania, virginia, west virginia
salamanders (clearcut oak-history forests in north carolina)
reduced canopy cover led to:
reduced soil moisture
reduced plant litter
increased bare ground cover
1st year: salamanders decline by 40%
2nd year: only one salamander found
4th year: no individuals
salamanders (pennsylvania, virginia, west virginia)
compared clearcut to single-tree management
clearcuts reduced salamanders by 70%
single cuts improved salamander habitat
mature trees increased horizontal structure; more canopy
more canopy increased soil/litter moisture
dead wood in forest management
use unmanaged sites for reference when possible
target species define management
natural vs artificial cavities
hardwood vs softwood
young vs mature snags/logs
artificial snags
What is a grassland?
Landscape dominated by graminoid (grass-like) plants. (>10% canopy cover)
Prairies
Steppes
Rangelands
Include woody vegetation
Prairies
Found on flat land or low elevations
Steppes
Found on mountainsides or high elevations
Rangelands
Used for grazing
Factors influencing grasslands
Precipitation
influences woody plant establishment, dominant plant type
Temperature
influences growing season type
Soil nutrient availability
Management practices (burns, plantings)
Factors influencing grasslands: plant structure
Woody plants/scrub important
perches: visibility
Cavities: nesting
Foraging of fruit, seeds, prey, etc.
Consequences of woody scrub:
may outcompete/shade out herbaceous veg
Encourage brood parasites
Encourage predators
Grassland conservation and history
Mass immigration to grasslands during 18th century
Continued use of plowing encouraged annual growth over perennials
Overgrazing and soil erosion led to dust bowl
99% of all grasslands in US either agriculture or rangeland
Managed lands to restore grasslands?
conservation reserve programs (CRPs)
conservation reserve enhancement programs (CREP)
Recreational/tourist hunting
Jointing vs non-jointing
Cool-season vs warm-season
conversion from cool season to warm season
Jointing grass
Internode elongation
Elevates growing point high up (can be “decapitated”)
Ex: big bluestem, Indiangrass, perennial rye grass, reed canarygrass, smooth bromegrass
Non-jointed grass
Vegetative (sterile) shoots good for grazing
Growing point (meristem) stays low
Ex: bentgrass, blue gramma, buffalograss, Kentucky bluegrass
Cool season (grasslands)
Optimum growth between 18-24C (65-75F)
Tolerate cold snaps, low temperatures
Spring and fall growth, inactive summer
Most non-native, mostly range forage
Warm season (grasslands)
Optimum growth between 28-32C (85-90F)
C4 grasses, often drought-resilient
Summer growth
“Big four”
big bluestem (Andropogon gerardii)
Indiangrass (Sorghastrum nutans)
Little bluestem (Schizachyrium scoparum)
Switchgrass ( Panicum virgatum)
Many non-natives
Why use fire?
promotes growth of-fire adapted species
frequency and intensity influences benefit
suppress woody vegetation
control invasive species (plants)
creation of snags
controls pests and parasites
increase bare ground (promotes colonization and regrowth)
encourage a landscape mosaic (more heterogeneity)
sources of ignition
natural fire
anthropogenic fire
natural fire
volcanic activity, lightning, other natural disasters
anthropogenic fire
man-made
deliberate fire
accidental fire
definitions of burns
based on vegetation
based on objective/goal
based on intensity
burn defined based on vegetation
forest fire, brush fire, etc
burn defined based on objective/goal
prescribed burn, hazard reduction fire, controlled burn, etc
burn defined based on intensity
ground fire
surface fire
crown fire
ground fire
burns ground vegetation, litter, and organic soil layer
occurs under drought or dry conditions
long, thorough burn
surface fire
burn litter, woody debris, and ground vegetation
dry conditions needed
intense burn (heat, vegetation)
difficult to control
crown fire
burns at level of tree canopy or crown
requires strong wind, steep slopes, heavy fuel loads
most intense (high heat, long duration)
extremely difficult to control
prescribed burn
application of fire to land to achieve a specific objective
under controlled conditions
requires a fire plan; objectives are clear and defined
low-intensity (ground or surface)
head fire
back fire
flank fire
safety
burn boss
cost efficiency
factors in a fire plan
objectives, goals
weather during burn
fuel
ignition material
crew logistics
fire behavior
factors affecting fire behavior
temperature
relative humidity
soil moisture
wind speed
fuel loads
topography
fire triangle
heat
fuel
oxygen
fire breaks
remove one of the main components of the fire triangle
blacklining
clearcuts
roadway
body of water
fuel types
1 hour - >0.25 inches in diameter
10 hour - 0.25-1inch in diameter
100 hour - 1-3 inch in diameter
1000 hour - 3-8 inch in diameter
prescribed burn environmental conditions
relative humidity
temperature
wind
prescribed burn relative humidity
ideal: 50-70%
below 50% too hot
above 70% can result in an uneven burn
prescribed burn temperature
ideal: 40-60F (4.4-15.5C)
prescribed burn wind
3-8 mph (4.8-12.9 kph)
prescribed burn methods of ignition
drip torch
fusees
flare gun
terra torch
DAIDs (delayed aerial ignition device)
head fire
fire burns in direction of wind
burns and spreads quickly
uncontrollable
backfire
burns against direction of wind
burns and spreads slowly
ideal for initial burns
flank fire
multiple burns that spread outward
overlapping flames burn out quick; no fuel
prescribed burn safety
firebreaks defined by wind, weather, and fuel loads
professionals; fire fighters on site or notified
methods to extinguish needed
burn boss
person in charge of prescribed-fire planning
ensures qualifications are met
obtains permits
monitors effects afterwards
prescribed burn cost efficiency
typically around $5 per acre
other methods (grazing, bulldozing, cutting etc.) are typically upwards of $30 per acre