Mountains and Plains
Riparian Landscapes
2-3% of land area
75% of native animals
Filter and store water
Continuously varied vegetation
Physical variables
Elevation
Climate
Grade
Soil type and depth
Sinuosity
Width: Depth
Human and animal impacts
orientation
*Riparian areas have moving, oxygenated water*
*Hydrophytes: Water-loving plants, legal boundary*
Rivulet to River
First-order stream
Willow, sedges, grass, meadows
Second-order stream
Formed by two first-order streams
Third-order stream
Formed by two second-order streams
Alder, water birch, willow
Abrupt vegetation shifts
Point bars
Channel bars
Cut banks
Terraces
Islands
Dams (log, debris, beaver)
Less sediment now
More likely to incise stream beds
Cottonwoods depend on flood-stage rivers to deposit seeds above the typical high water mark
Shifting riparian mosaic
Changed by flood suppression
Each pound of plant material uses ~400 lbs of water
People benefit from beaver soils
Soil stability
Longer flow, bank storage
18x more water storage
Beavers used by people to fill in gullies need appropriate building materials
Aspens preferred, will use tires
More gullies now than in the 1700s
People love riparian areas!
Higher land prices
Increased recreation
Just plain pretty
Livestock
Concentrate where food, water, and shade are (aka riparian)
So did bison
Fencing, herding, salt licks, keeping cattle out
Consequences
Bank erosion
Lowered bank storage
Lowered water quality
Decreased habitat
Fewer fish
Reservoirs
“Headwaters of the West”
85% of water goes out of state
Decreased riparian habitat
Short-lived benefits
Sedimentation
Flood control
Irrigation
Power generation
Recreation
Great fluctuation in water level
No plants can grow
Levees reduce the riparian area
Dikes increase it
Irrigation
Firm need
Any means necessary
Only 2-3% of Wyoming is arable
Creation of ephemeral streams
Lack of protection under the Clean Water Act
Poor fish habitat
Return flow
More water downstream (+)
90% loss from evapotranspiration (-)
Nutrient leaching (-)
Eutrophication (-)
Salt deposits (-)
Invasives
Beavers removed
Banks logged
Floods created
Sluice dam?
Species
Canada thistle
Leafy spurge
Yellow sweet clover
Kentucky bluegrass
Smooth brome
Russian live
Salt cedar (tamarisk)
Non-edible
Halophile, salt-secreting
Higher transpiration
Non-Riparian Wetlands
Marshes, playa, wetlands, wet meadows, fens
1974 National Wetlands Inventory
950,000 acres
1.5% of Wyoming
5% permanently flooded
2,692 Wyoming plant species
12% oblate wetlands
13% facilitative wetlands
Important plants
Sedges (Cyperaceae)
Grasses (Poaceae)
Willow (salicaceae)
Mosses
Algae
Amphibian habitat
Seasonal drying keeps predators to a minimum, which is good for the environment
Prolonged saturation creates oxygen deficiency
“Gleyed horizon” from mineral leaching in soil
Carbon sequestration
Aerenchyma: a spongy tissue in the stem that lets oxygen diffuse
Toxicity
Reduced sulfur
Reduced iron
Reduced manganese
Rhizosphere: mm thick layer adjacent to roots
Oxidation occurs here and renders compounds harmless
Red soils are often hydric soils
Diversity maximized at wet/dry fluctuation
Marshes
Med, muck, or sandy bottoms
Common in potholes
Beheaded streams
Old beaver dams
Often form rings of various vegetation, sorted by drought tolerance
Increases biodiversity
Playa Wetlands
Salt-precipitated wetlands most often occur at low elevations
Halophytes (salt > 5 parts per 1000)
Greasewood
Red swamp fire
Saltgrass
Devoid of life much of the year
Wet Meadows
Where water tables are at or near the surface of the water, but the water table drops in the summer
Hard to recognize
Hydrophytes
Hydric soil
Graminoid vegetation
Develop below glaciers and snow banks
Graduated growth
Can be damaged by overgrazing
“Plugged” changes species abundance
Desirable real estate
Fens
Rich in graminoid vegetation, but willow is the most common
Not a bog, pH too high (5-8 for basic fen)
Different water source
Mosses do well
Fens can merge with mashes, peat floats
Classified based on mineral richness
More minerals at a more basic pH
Management issues
35-40% already lost
Groundwater contamination
Peat mining
Invasive plants
Reed canary grass
Hybrid American-European descent
Highly aggressive
Broadleaf and Narrow-Leaf Cattail
Serile
Rhizomes
Purple Loosestrife
Colorful 3-4ft tall
Invasive seasonal springs
Climate change
Increased droughts
conversion into playa
Peat deposits decompose by adding carbon dioxide
“Wetlands Reserve Program”
Landowners paid to protect wetlands
Artificial wetlands are often built to offset new development on existing wetlands
Grasslands
Plains east of the Rocky Mountains
2 Types
Shortgrass prairie
Southeast corner of WY
Buffalo grass, blue grama
Mixed-grass prairie
17% of the state
Bunch grasses
Blue gramma
June Grass
Sandberg bluegrass
Indian ricegrass
Forbes, shrubs, and succulents
50 species per acre
Plant communities are good indicators of soil types
Soil types
Sandy
Aridisols
Mollisols
Grassland invasion
All of the world
Less frequent fires
Overgrazing
Atmospheric changes
Soil Aeration
Badgers, ground squirrels, harvester ants, pocket gophers, prairie dogs
Survival
75% of biomass is below the ground
Most herbivores are vell
Invertebrates are the largest group of herbivores
70% of roots in the first 4 inches of soil
Most perennial buds at or near the soil surface increase protection from fires and grazing
Buds will replace blades killed by herbivores or fire
Intercalary meristem on a leaf
Special meristem below ground
Energy stored in roots allows regrowth
Xerophyte
Drought-tolerant plant species
Small leaves
Pubescence
Light coloration
senescence/ drought deciduous
Animal adaptations
Continuous tooth growth (20 mya)
Ruminant digestion
Coevolution leads to dissimilar diets
Partitioning Resources
Plants use the same resources at different times of the year
Use different soil depths
Grass vs forb herbivory
Physiological differences
C3 metabolism in cool weather
C4 metabolism in warmer weather
Energy Flow
Photosynthesis <2% efficient
Reflected energy
Evapotranspiration
Soil heating
500-900 g/m2
“Coarse soils have higher percolation rates, meaning greater water need.d”
Patchy rainfall causes episodic growth and large mammal distribution
Pathway of solar energy
65%-85% moved internally
30-40% for maintenance
A large portion of stems and leaves
10%-30% lost to herbivory
33% large herbivores
33% nematodes
33% insects
1% birds and small mammals
Energy flows; it doesn’t cycle
Nutrient cycling
Nutrients are lost from a system mainly by erosion
Gained by weathering
Grasses are high in lignin and cellulose and decompose slowly
This leads to higher infiltration rates
Increases microbial decomposition
Creates beautiful, fertile soils!
Low rates of nutrient leaching due to low rainfall
Fabaceae plants fix nitrogen
93% of other sources of nitrogen
What are they, and how does nitrogen fixation work?
Fertilizing rangelands
More forage
Higher protein content
Selectively graze fertilized areas
Favors undesired weeds
Not economically viable
Nitrogen that is part of a plant is often stored in the perennial parts of that plant and thus stays in that plant. (50%-80%)
Disturbance and succession
Secondary succession: changes that occur after a disturbance that brings the system back to baseline
Types
Plowing
Drought
Fire
Grazing
Burrowing animals
Recovery is often quick if the roots are intact
Damages are often cyclical
Effects of Grazing
Light grazing makes plants grow faster and with higher ground cover
Mechanism:
Removal of senescent leaves
Removal of transpiration sites
Concentration density in waste
Removal of “apical dominance”
Compensatory growth hypothesis
Little evidence as of 1993
Clipping increases photosynthesis by 5-10%
Less than the clippings would have added
More evidence of bison recently?
Some rangeland is still recovering from the 1800s and early 1900s practices
Grasslands with native grazers tolerate grazing better
Should ranges be managed for ecosystem services?
Gnu and impala symbionts on “grazing lawns”
Prairie dogs create prime forage
Fire
Frequent in pre-fire suppression years, lots of fuel buildup
Fire is low in prolonged drought
10-25 lightning fires per 1000 miles in the Great Plains
Most frequent in July and August
Fires every 2-25 years
Less in arid or steep areas
Warm-weather species are more tolerant than cool-weather species
Natives burned areas to attract game
Allows soil to warm quickly
Creates less mulch
Very little loss of nitrogen
Increases evaporation
Patch-burn grazing systems
Exposed to both
Benefit cattle and birds
Drought
Decreased carrying capacity
Some plants increase with a lack of competition
Plant cover is reduced to 2% in extreme droughts
Prickly pears are the last strongholds for plant survival
Above-average rain can convert the prairie as well
Grasshoppers
The most important animals in the western grassland!
Outbreak during droughts
Unknown reason
Correlation, not causation
.05% of veg or 65% of vegetation, depending on numbers
Cut 25x more than they eat
Control measures only last a year
All species are native
Rocky Mountain locust extinct as of 1900
Burrowing animals
Pocket gopher mounds can cover 25% of the grassland
Skunks and badgers amplify gopher mounds
Burrows provide habitat
Mice, beetles, crickets
Prairie dog
Black-tailed and white-tailed
3ft-9ft burrows
Improves water infiltration
Habitat creation
Keystone species and ecosystem engineer
Build colonies in heavily grazed areas
Will clip the grass to better see predators
Reduces livestock forage
Viewed as a nuisance
Provide long-term benefits to the land
Sylvatic plague
Flea transmitted
Deadly to prairie dogs
Introduced in the 1800s
Kills ferrets too
Ground Squirrels
0-100 per acre
Unknown reasons for population variance
Harvester ants
Pogono
Invasive Plants
Effects
Crowding out
Altering food availability
Carbon storage capacity reduced
Nutrient availability
Increased erosion
Species
Canada thistle
Russian thistle
Cheatgrass
Combatting
Maintenance of native species
Finding herbivores
Lowering soil nitrogen
Herbicides
Challenges
Nothing that looks original exists
Need to establish a park mandate
Objections to bears and wolves
Increased prairie dogs
Increased ferrets
More land is needed for agriculture
Oil, gas, and wind farms
Diseases and invasives
Climate change
Sagebrush
Artemisia tridentata
⅓ of Wyoming by area
12 species
Indicate deep soils
Usually in arid areas
Biotic communities similar to grasslands
Reliant on deep snow
Can reach water at great depths
High genetic diversity
Low sagebrush
Mountain big sagebrush
Mountain silver sagebrush
Big basin sagebrush
Wyoming big sagebrush
*All found in the GYE
Adaptations:
Distribution is determined by delicate seedlings, not adults
Most seedlings in wet years
Any disturbance to the sage lowers ecosystem productivity
Hydraulic redistribution
Deep roots bring water to the soil's surface
Can reverse this process at any time
Nurtures bacterial communities
Prolongs growing season
Efficient water use
Rapid stomata closing lowers transpiration
Evergreen
No downtime in spring
Produce ephemeral leaves as well
Pale color and short hairs on leaves
Keeps the plant cooler, lowering transpiration rates
Carbohydrates are stored in twigs
Good food source
Evolved terpene defense
Vary by species and individuals
Cannot sprout from roots
Longevity and seed production are important factors in a community
100-year lifespan
50 is very common
Produce 1000s of seeds each year
Seeds vare iable for 4 years
Not salt-tolerant
Discontinuous clustered growth
Only sprouts in favorable years
The Sagebrush Ecosystem
The presence of aromatic shrubs with deep and shallow roots
A large portion of precipitation occurs during the winter season
*Many similarities to grasslands!*
Hydrology and Plant Growth
Makes ecosystems more productive
80-250g per square meter per year
> mixed grass prairie
Black body effect
Causes snow to melt around the plant
Fills in with drifts
Reduces sublimation
Energy, Carbon, Soil, and Organics
~½ food chain occurs underground
Less palatable than grasses
Winter forage for:
Pronghorn
Mule deer
Elk
Takes >10 years to sprout post-fire
Great carbon storage
Soil retention is a key to reestablishment
Carbon dioxide
Sink during wet years
Source during dry years
NPS manages for:
CO2 sequestration
Resistance to invasives
Habitat for endangered species
Nutrient availability
Water is more limiting than nutrient availability
Stems reabsorb some nitrogen from deciduous leaves
More above-ground biomass than in grasslands
Recovery after Disturbance
Increases with precipitation
Increases with soil litter depth
Decreases with grazing
Decreases with herbaceous competition
Increases with more seeds
Increases with mycorrhizal nets
Decreases with mine tailings
Drought, Frost, Extended Wet
Some winter mortality
Water stress
Late frosts
5 years of wet phase causes extensive die-offs
Likely to become more common with climate change
Grasshoppers
Potential to kill 50% in warm, dry years
Fires
Natural interval of 20-100 years
Emerging research says 70-250-year interval
Cheatgrass (Bromus tectorum)
Benefits from disturbance
Found above 7,000 feet
Climbing with climate change
Introduced in the 1800s fromthe European steppe
Grow in late fall and very early spring
Gets a head start on native species
Lower biological soil crushes
Increases fire frequency
Increases grazing but only before it flowers
Increases with warming temperatures and CO2 levels
Effects on Livestock
Grazing is not a disturbance unless there are too many animals or for too great a time
Decreases biological crust and leaves areas vulnerable to invasive species colonization
Horses
Evolved in North America
Died out 10,000 years ago
Reintroduced accidentally in 1539
DeSoto dropped 220 around Florida
In the 1600s, Indians acquired and freely traded horses
Dramatic lifestyle changes followed
An estimated 3,500 feral horses in WY as of 1995
Periodic round-ups
Research on birth control
Sage Grouse
Jeopardized and declining
Habitat loss is the main driver
Inappropriate grazing
Population fragmentation
Federally listed as endangered
50% decline in 10 years over the 80s and 90s
Eats sagebrush leaves
Also, insects and forbs
Range of 30 square miles
Always use the same lek
Will not change and is slow to abandon
Noise sensitive
Tall structures encourage raptors
Increases predation
Vulnerable to West Nile virus (has caused large die-offs)
Escarpments and Foothills
Often glacial moraines
Small slivers of the ecosystem
Important for big game
Provide forage and shelter
Gros Ventre and Slide Lake
Vegetation banding due to soil types
Trees grow only on ridges
Very little fire fuel
Plants and Adaptations
Mountain Mahogany Shrublands (Cerocarpus sp.)
4,500ft-8,000ft
Curl-leaf: evergreen
Birch-leaf: deciduous
Nitrogen fixer
Curl-leaf controlled by fire
150-year cycle
Juniper Woodlands
Utah Juniper is common in western WY
3,600ft to 6,000ft
Expansion and infilling
Livestock grazing
Fire suppression of >30-60 years
Grow well under sagebrush
Range expanding with climate change
Ponderosa, Limber Pine, and Douglas-fir
The 20th century has seen an increase in all 3 species
Reduces the forage available
Increases transpiration
Lowers stream flow volumes
Needles are toxic to consume
Ponderosa
Low elevations
Summer rains
Eastern Wyoming resident
Mowry shale substrate
Limber Pines
Dryer and cooler environments
Extreme elevations
Rocky soils and ridges
In the lee of boulders
Douglas-Fir
Dominant species in western WY
Fires every few decades
Mixed foothill shrubs
Many nitrogen-fixing species
Serviceberry
Utah and Saskatoon
Higher fire rate
Snowbrush ceanothus
Fire obligate
Greasewood
Water seep obligate
Foothill grassland
Shallow snows
Shallow soils
Very windy
Cushion plants
Deciduous woodlands
Aspen, chokecherry, gamble oak, Bur oak
Mesic sites: high water content
Deep soils
Chokecherries
Woody draws
Eastern Wyoming
Aspen
North-facing slopes with snowpack
Water seeps
Aspen atoll
Ring of aspens around a seasonal drift
Plant and Animal Interactions
Elk prefer to winter here
Aspen, Elk, Fire community cycle
Aspens
Clonal species
Each clone lives ~150 years
Large die-offs
Fire suppression
Elk browsing
Linked to hunting, feeding, and few predators
Cattle contribute
Aging out
Wintering grounds for all herbivores
Summer forage determines winter survival
Used more heavily during the winter months
Deep snow uses more energy
Shorter growing season
Ungulates create browse lines on stems
Typically recover quickly
Mule Deer die-offs
Drought due to climate change
Habitat fragmentation
Mitigated by feedlots
Overgrazing of the surrounding forests
Disease transmission
Increased hunting opportunities
Decreased ranching conflicts
Pine seed dispersal by birds
Pinyon and Limber pines
Large nutritious seeds
Clarks nutcrackers
100 seeds per beak pouch
Demonstrated moving seeds over 13 miles to caches
Collected late summer and buried on south-facing slopes
Range overlaps with pines with large wingless seeds
Selectively cache seeds in burned areas
Mountain Forests
50 mountains above 13,000ft in Wyoming
No 14,000ft peaks
Important sources of water and timber
Variation in Mountain Environments
Elevation
Steepness
Aspect
Bedrock
Soil development
Snow accumulation
Temperature
2-5 degrees per 1000 feet
Growing season
Survival in the Mountains
Short, cool, dry growing season
Photosynthesis occurs near 0 degrees
Evergreen and wintergreen plants
Tolerate cold to -76
Low-nutrient-content soils
Persistent leaves
5-18 years on Lodgepoles
Mycorrhizae nets
Seed establishment
Develop early
Mycorrhizae attachment at 2 weeks
Mammals
Migration
Insulation
Torpor or hibernation
Large feet
The Forest Community
Buffaloberry
Dwarf huckleberry
Ground Juniper
Heartleaf arnica
Lousewort
Pyrola
“Mycoheterotrophic”- lacks chlorophyll and obtains energy from dead tree roots via saprophytic fungi. Ex: pinedrops
Undergrowth is inhibited
Snow cover
Dense tree cover
Plant parasites
slow/reduce growth
Deform and kill
Examples:
Dwarf mistletoe
Comondra blister rust
Requires 3 plants in close proximity
Lodgepole, sagebrush, and ribes members
Causes top kill, not death
Animal effects
Cervid grazing reduces new tree growth
Birds increase seed dispersal
Red squirrels increase tree germination
Prefer serotinous cones
Evolved more powerful jaws
Reduced serotinous trees
Variation with elevation
Creates a beautiful mosaic based on microclimates
Disturbance over time
Big and small, swift and slow
Forest fires
Frequency vs severity
Most frequent in the foothills
High elevation is more moist
Limited effect of historic fire suppression
Intensity: BTU/minute
Severity: based on after-effects
Litter fires to crown fires
Forest can be characterized by their fire prevalence
Burn areas attract wildlife
Bark beetle outbreak
Many species of beetles
Mountain pine beetles are the most common
All are native
99% of beetles prey on dead wood
Tree-killing species all have similar life histories
Attack all pine trees
Life cycle
Emerge from the bark in July and August
Target larger trees
Females drill through the bark and cut egg galleries
Healthier trees use resin to expel invaders
Also toxic compounds
Females secrete aggregating hormones inside infected trees
Once colonized, they release a disaggregating hormone
Females carry “blue-stain fungus”
Infect and kill in less than one year
Larvae eat fungi and the cambium layer
Larvae “cold harden” in winter
Vulnerable to early fall freeze
Warmer temperatures cause drought stress in trees and kill fewer beetles
Positive feedback loop until colder temperatures or fewer trees
Never kill small trees
Allows smaller trees to grow 2-3 times faster
80 years to reestablish
30 years into the GYE study
Major Forest Types
Rexford Daubenmire Habitat Type
2 criteria
Undistributed dominant species
Understory plants
Ponderosa pine forest
The most widespread tree in the West
Summer rain dependent
Warmer climate needed
Migrating northwards
Frequent low-intensity fires
Moisture determines density
Episodic recruitment
Douglas-Fir Forest
Sometimes found with ponderosa
<8,500 feet
Wetter sites
Limestone and sedimentary strata
Wet areas burn more often (paradoxical)
Become more dense
Invading sagebrush
Lodgepole Pine Forest
The most common tree in WY
6,000-11,500 feet (latitude dependent)
Loves granites and rhyolites
Episodic development
Infrequent fires (100-200 years)
Severe and widespread fires
Serotinous cones
Not all trees make serotinous cones
Trees usually all or none
Varies by forest age
More non-serotinous cone trees than serotinous ones
The red squirrel population influences the cone-type
Low-elevation trees have more frequent serotinous cones
Fewer in high elevations
Due to different rates of crown fires
Forest management for both types?
“Canopy seed banks” and fire intensity determine new recruitment
5-100,000 per acre after the ‘88 fire
Lodgepole mono-cultures are usually serotinous
Mixed stands have fewer serotinous cones
“Dog-hair stands”
Difficult to walk through
Survive for 100 years or so
< 4-inch tree diameter
Produce seeds
Average density of 500 trees per acre
80% of trees in YNP are lodgepoles
Other disturbances
Blister rust
Dwarf mistletoe
Bark beetles
Root rot
Wind storms
Lodgepoles have seen little change with humans in the landscape
Climate change is the biggest danger
Spruce- Fir forests
Engelmann spruce and subalpine fir occur together
Lower temperatures for seedlings
More water
Lower water use efficiency
Capable of vegetative reproduction
Infrequent fires
Those that do come through are hot and stand-replacing
0-150 years mixed spruce and fir
150-250 fir trees dominate
> 250 years spruce dominate
Insect outbreaks
Spruce beetles
Target old stands
Can reproduce in recently dead trees
Western balsam bark beetle
Kill large sections of fir
Favors warm, dry conditions
Abundance
Spruce
Dominate older stands
Live 500+ years
Low establishment rate
Fir
Dominate young stands
Live 250 years
Establish quickly
Forests today resemble those of the 1800s
Aspens
Occupy depressions and wetter environments
Use less water than lodgepoles, but seedlings need more
Grown in places that favor evergreen trees
Refixes its carbon dioxide
Dwarf Huckleberry does the same
“Evergreen- deciduous”
Seedling establishment is rare
Seedlings are wet-footed
Will grow in recently burned areas
Individual “trees” (ramets) live 100-150 years
10,000 ramets per acre, 3 feet tall after fire
Often replaced by fir
Large ramets suppress new shoots using hormones
Fire cycles of decades to centuries
Heavily affected by browsing
Photos show aspens in decline
Many fires pre-1800s
Plants killed by root rot
Canker disease
Browse and beaver-cutting
SAD (sudden asphyxia death)
Severe drought 2000-2003
Wildlife
Permanent: blue grouse, boreal owl, beaver, lynx, marten, red squirrels, snowshoe hare
The Forest Ecosystem
Tree Growth
Forest development
Soil maintenance
Water quality
Disturbances
Energy Flow and Productivity
1-3% of solar energy hitting the canopy is used for photosynthesis
Most energy is used to evaporate water
Low growth rates, relatively
Younger forests have higher growth rates
“Primary productivity”
Soil litter accumulates quickly
Mostly leaves, branches, and fallen trees
High C:N ratio
Fire important decomposer
15% of primary productivity is related to mycorrhizal nets
2% of the energy fixed by plants flows through animals
Hydrology of Forest Landscapes
High elevation receives more water than can evaporate
PE > 1
Water towers of the west
50-75% due to snowfall
Surface water drainage
Snow drifts
2-5 inches of water per foot
National Resource Council estimates total water (“snowtells”)
Soil water capacity
The amount of water soil doesn’t lose to the downhill flow
Depends on the water already in the soil
Increases with deep soil
Increases with fine soil
Increases in the summer months
Weather and Climate
Rapid melting means less transpiration
Cold springs are better
Fall
Rains lower capacity
Early snow means soil remains unfrozen
Little to no moisture from south-facing slopes
Percolation percentage
Igneous and metamorphic imperious
Increases runoff
Farms often occur near sedimentary rocks
Vegetation type
Total leaf area
Leaf type (evergreen vs deciduous)
Increases interception
Increases transpiration
Lowest with low area and deciduous
80-90% from meadows
60-65% from forests
20% from lodgepoles
Water content
Landscape mosaic
Most water when forests and meadows mix
Maximized when
30%-40% of the landscape is harvested with patches of 2-5 acres
Larger openings have too much wind
Nutrient Cycling in Forests
Longer-term cycle
Nitrogen most well-studied
78% of the atmosphere
Must be converted from nitrogen to ammonium or nitrate
Root nodules
Lightning
Decomposition
Some plants absorb nitrogen from the soil as amino acids
Leaching potential
Highest in 3-6 weeks of snowmelt
“Spring flush”
Nitrogen is retained because plant uptake is extremely rapid
Inputs
Dryfall
Wetfall
Rock weathering
Animal immigration
Runoff
Fixation
Undisturbed lodgepole forests accumulate nutrients over time
Deadwood accumulates nitrogen
Critical nutrient source
Plants have high retention rates
Withdraw nutrients from sensing tissues, ~half of nitrogen is reabsorbed
Higher in lodgepole pine
Soil nitrogen is very low, <1%
Slows decomposition
12-22 years for leaf decomposition
100 years for Tree Bole
Effects of Forest Disturbance
Fire (depends on temperature)
Low intensity
Foothills
Ponderosa and Douglas-fir
Rapid recovery
Burn litter and small trees
High intensity
Reduce leaf area
Spruce and lodgepole
Kills everything
Erosion
Increases with fire intensity
Increases with slope angle
Increases with area burned
Decreases with water infiltration
Decreases with understory development
Summer rains cause more erosion than snowmelt
Leaf area
Returns to normal after decades
Depends on the number of saplings
Leaf area maximum at 250 years
Aspens and lodgepoles recover quickly
Nutrient cycling
Volatilized by heat
Higher probability of nutrient loss
Higher nitrate levels in streams
Post-fire “luxury consumption”
Plants take more nitrogen than necessary
Nitrogen replacement in 40-70 years
Living biomass important
Insects
Target the largest trees
Reduce total growth for years
Other plants grow faster
Years- decades of recovery
Decreases transpiration
Increases in soil moisture
Short-term nitrogen boost
More research is needed
Timber Harvesting
Clear cuts
Increases
Stream flow
Nutrient loss
Undergrowth
Soil remains intact
No shade
No “bole wood”
1-4 years for shrub recovery
Lower decomposition rates vs fire
If a slash is left, nutrient levels are high
Deadwood provides a critical habitat for wildlife
Better moisture retention with trees
Long-term benefits from more slang and large wood (twice the normal)
Less burning of slash
Erosion is higher with fires
Periodic erosion is good for stream biodiversity and productivity
Green tree retention
Creates bird perches
Half cut means twice the water runoff and no additional nutrients
Clear cut means 3 times the water runoff and 6 times more nutrients
Dwarf mistletoe
Native species
Lowers productivity
Typically controlled by fire
Soil erosion is the largest concern
Windthrow in cut patches
The Future of Mountain Forests
Fragmentation
Roads
Logging
Homes
Climate change
Bark beetles
Precipitation
Longer fire season
Higher evapotranspiration
Reduced water for human use
Upward shift in forests
Type conversions away from forests
Reduced water supply
More cutting, more water
It would require high-elevation cutting
That wood is valued for other reasons
Fires
Upsurge in the last 25 years
Inadequate forest management
Too much fire suppression
Too little harvest
Too ubiquitous to be true
Fires and beetles
Moderately burned trees are more susceptible
Drought stress is more likely
Beetles and Fire
4 stages
Green, red, gray, dead
Torching vs crown fires
Small to undetectable changes
Increase in torching
Management options
Allow insects and fires in the backcountry
Well-adapted resilient ecosystem
More fires are still okay
Nature's resilience against humans
From country
More homes and infrastructure
Timber harvesting
Local control
Reduce vegetation density
Build with non-flammable materials
“Firewise” practices
Fire or Fuel breaks
Large fires from predictable winds
Recognize fire risk and discourage homebuilding
No clear stance on whether to remove beetle kill
Aspen forests as a bellwether
Wonderful biologically and aesthetically
SAD (sudden aspen die-off)
Worst on large old aspen trees
Highest from 2003-2007
Concentrated in Colorado and Utah
Triggered by drought and high temperatures
South-facing slopes are more vulnerable
Low elevation
Low water capacity soils
Evidence increasing
Recovering very well at higher-than-average elevations
Suggests that aspens are already responding to climate change
Likely to continue
“Bioclimatic Envelope”
- shows aspens 1000 feet higher than historically
Total decrease in range
Similarly, all forests will shift
Decline from 15% of WY to 7.5%
Yellowstone will convert to all Douglas-fir
Increased habitat fragmentation
Mountain Meadows and Snow Glades
Referred to “Parks”
Highly Variable Plant Species
Why no trees?
Too much moisture
Fire soils, river banks
Too much competition from grasses and forbes
Soil differences!
Cinnabar Park, Medicine Bow
Most well studied
Due to the shallow 6-inch fine soils, there is a better grass habitat
Trees' habitat means coarser soil and thicker soils
Trees are also stressed by blown ice and snow
Subalpine meadows persist where summer frosts are common
Caused by direct exposure
Reduces sapling recruitment
Snow glades and Ribbon Forests
Snow glades: meadows created by late-lying snows
The growth season is too cold, wet, and short for trees
Favor mold growth on saplings
Too many pocket gophers
Seedlings have difficulty establishing themselves with too little or too much snow
Insufficient moisture
Insufficient protection from abrasion
18-56 inches is the sweet spot
Ribbon Forests
Initial establishment is a mystery
Fire?
Aspen atolls
U-shaped or doughnut-shaped aspen groves
Established by the “snow-fence” effect
Center becomes clear
Economically important areas
Lots of water, no use
Increases stream flow
Occasionally created artificially
Livestock grazing on meadows
Meadows have a higher carrying capacity than the range
Verticality (green wave)
Variability in the snowpack
Diverse plant communities
Ranchers move to high elevations as soon as the soil is dry enough
Grazing is restricted to the short summer season
Most have a shepherd
Fewer animals
Meadows are shrinking back to their natural size
Reduced by mining
Reduced by logging
Increased by fire
Forest: meadow ratio is a climate indicator
Forest Expansion into Meadows
Reduced by fire
Increased by grazing (less competition)
Climate
Warmer means less frost and more saplings
More vapor means warmer nights
Climate Response
Water uncertainties
Down prediction accuracy
Minimal effects on growth
Large effects on stream flow
Water may not be a limiting factor
Upper Treeline and Alpine Tundra
11,500 feet (South facing) to 9,800 feet (North facing)
The slope aspect is a major factor in the treeline and higher on south-facing slopes
Krummholz
Common Trees:
Engelmann spruce
Subalpine fir
Limber pine
Whitebark pine (GYE only)
German for twisted wood
Commonly flagged
Need:
Moderate snowfall
Shield trees from winter
Other plants
Shield from summer and sky
Safe when large enough to gather snow
Often grow in slight depressions
Increases access to water
“Layering branches pressed into the ground by snow grow roots
Create tree islands
Treeline formation
1000 feet = 300 miles = 5 degrees F
Wind
Temperature
No trees where the growing season is <3 months or below 43 degrees F
Shrubs and herbs are better adapted
Decreased photosynthesis needs
Tree adaptations:
Clustered needles
Less transpiration
Flexible branches
Avalanches
Leeward mountain sides
End in the “runout zone”
Shrubs common as snow movement happen within the snowpack
Trees > 4 inches in diameter break
Every 50-100 years
Blister Rust
Invasive
Fungal parasite
Mainly kills whitebark, limber, and bristlecone pines (white pines)
Secondary Ribes host
One two-punch with mountain pine beetles
Survival
Many plants are also found in the Arctic
Differs from Arctic
High-intensity light
Larger temperature swings
Shorter days
No permafrost
Increased evapotranspiration
Low pressure
High winds
Decreased water uptake
Poor, cold soil
Low nutrients
Rapid freeze-thaw cycles
Most plants are herbaceous perennials
Lichens common
40-300 grams per meter per year
30-75 day growing season
Adaptations:
Cold tolerance
Ever and wintergreen leaves
Photosynthesis under snow!
Shallow, spreading roots
Mycorrhizae network
Grow and mature more rapidly at higher elevations
“Cushion: growth pattern
Dense mats, close to the soil
Phlox
Reproduction largely vegetative
Large petals act as windbreaks for insects
Apomixis: reproduction without pollination
Numerous animal adaptations
All warm-blooded
Tundra Mosaic, Frost, and Burrowing
Types of tundra
Fellfields
Alpine turf
Wet meadows
Willow thickets
Abiotic
Snow beds
Talus slopes
Boulder fields
Water
3 spatial scales
10’s of miles
Changes due to local climate
Scale of feet
Changes due to boulders and their ability to absorb heat
Intermediate scale
Topography and tree islands
Cryoturbation
Freezing and thawing of moist soils, days to years
Freezes push the largest boulders toward the surface, creating “patterned ground”
Solifluction
Soil becomes saturated and moves downhill
Two phenomena combine with the burrowing animals' activity to constantly disturb the soil
“Is there a 'stable' alpine ever?
Nitrogen Deposition
Nitrogen is a limiting factor
Some nitrogen-fixing plants
Nitrous Oxide pollution leads to nitrogen saturation
Net 0 nitrogen in the alpine
Accumulates in snowbanks
Leads to eutrophication
Decreased fish numbers
Increased willows
Advancing Treeling
Relictual hypothesis
Current trees only tolerate our climate as adults, no recruitment
Treeling lags behind the climate by 50-100 years
The Uinta Mountains show a treeline increase of up to 550 feet
Paradox- early snow melt increases frost damage to plants
Snow cover delays development
Animal impact
American pika
The Greater Yellowstone Ecosystem
Introduction:
40,000 square miles
2 National Parks
7 National Forests
10 Wilderness areas
3 Wildlife refuges
14 mountain ranges
3 major river systems
Early Western explorers referred to YNP as Wonderland
631,000 years ago was the last major eruption
3 inches of ash in Iowa
9 million YBP- Teton uplift
50 miles
Precambrian rock
Flathead sandstone is now 6 miles below the surface
12 inches per century
Pinedale Glaciation: most recent
Began 80,000 years before present
25,000 ybp maximum
4,000 feet thick
An ice dam flooded Hayden Valley
Glaciers until 9,000 years ago
Primary succession
14,000 ybp park was mostly tundra
11,500 ybp Engelmann spruce colonized
9,000- 11,000 whitebark and subalpine fir
4,500-9,500 ybp douglas-fir
Yellowstone National Park
Ancestors of modern tribes 8,000-11,000 years ago
Food
Obsidian
3,486 miles
150 lakes
5% of the park
Mostly rhyolite (infertile soils)
70 inches of precipitation in the south
10 inches of precipitation in the north
“Finest trout fishing in the world”
80% forested
Lodgepole pine is the main tree tolerant of poor soils
24 habitat types where lodgepoles are the dominant plant
From low to high
Whitebark
spruce/ fir
Lodgepole
Douglas-fir
Aspen
Cottonwood
Grand Teton National Park
1872 Hayden Expedition #2
Detachment sent to Jackson Hole
Included William Henry Jackson
1897 town of Jackson
1906 Snake River Dam
1989 dam reinforced
Pierce Cunningham
Circulated a petition in 1925 asking WY to set aside the valley as a national park
Accomplished in 1950
Compromises on grazing and hunting
Vegetation of Jackson Hole
58% non-forested
Tundra, boulder fields, meadows, grasses, and shrubland)
28% lodgepole
7% Spruce/Fir
4% Douglas-fir
1% Aspen
Whitebark pine is common on higher slopes
Much of the Tetons are above the treeline
Lichens only
Sagebrush Mosaic
Glacial outwash plain
Deposits of glacial melt 80,000 to 12,000 years ago
Mountain big sage and Idaho fescue
East of Snake River
Deep soils, more water
Mountain big sage and bitterbrush
Sandy soils and gravel
Low sage and mountain big sage
Shallow infertile soils
Gros Ventre Landslide
Mountains are diverse
Volcanics (50 million years old)
Gravel conglomerates
Sedimentary strata
Granites and gneiss of Jackson Peak
June 23, 1925
1 mile long
Half a mile wide
300 feet deep
900 x 200 ft dam
3-mile-long lake
The dam failed 2 years later
6 people died
The top 20 feet of the dam washed away
20 20-foot wall of water hit Wilson 2 hours later
Management Issues in GYE
Initial objectives
Protect the hydrothermal from vandalism
Protect wildlife from poachers and predators
Protect vegetation from fire and overgrazing
Elk proliferated: threatened the persistence of aspen, willow, and grasslands on winter range
Grizzly neared local extinction
1963 Leopold report
Wildlife management in the national parks
“Let ecological processes operate to the greatest degree possible, with human intervention allowed as needed for safety or to correct problems caused by previous human activity.”
1968 elk culling (all culling) stopped
Continuing debate onthe long-term effects of Native Americans
The Elk Problem
By 1912, we had 30,000 elk in Yellowstone
Trapped and shipped to other places
Cullings
Loss of willow and aspen habitat
Important habitat for migrating birds
Competition with deer and beavers
1912 National Elk Refuge
Reduced agricultural conflicts
Increased herd sizes
Decreased starving animals
Increased habitat destruction
Increased disease transmission
Decreased habitat conservation
The key winter range north of Yellowstone National Park was purchased or protected
Do elk harm northern range vegetation?
“Northern range is different from when Europeans arrived, but the ecosystem is not in imminent danger of losing any major piece.s”
National Academy of Science (1998)
Less dramatic damage than the Aspen and Willow communities
Increased compensatory grass growth
35-85% higher than enclosures
Most grazing takes place in winter and fall when vegetation is dormant
1982, Biologist Doug Houston concluded that no herd reduction was necessary
85% of aspens established before 1920
Neither fire nor climate was sufficient to explain this
40,000 elk in 1968
19,000 elk in 1998
Fire management
The systematic elimination of fires started in 1886 with the arrival of the US calvary
Ineffective in more remote regions of the park
1963 Leopold report
Set theme
1972
Lightning caused fires to burn without interference in a remote portion of the park during moderate weather conditions, when the risk of human injury or serious resource damage is minimal
1972- 1987
235 fires
1- 7,500 acres in size
Only 27 are larger than 1 acre
1988
1.4 million acres
25,000 firefighters
$120 million
More by drought and wind than fuel build-up
North Fork Fire 490,000 acres
The cost of fuel reduction would be reasonable compared to the cost of fire
Increase in aspen seedlings in burned areas
TRUE SEEDLINGS!
Increased visitation
Today’s policy is similar to 1989
Climate models
By 2050, large fires could occur nearly every year
The fire cycle of 120-300 years could shift to <20 years
Fire Cycle: the time for a whole system to burn
Decreases in old growth
Type conservation of major species
Beetles, blister rust, white-bark pine
White-bark pine: common at high elevation
Important grizzly food
Recover from fire via distribution by Clarks nut-crackers
White pine blister rust:
Non-native
Global warming
Mountain pine beetles invade at high elevations
Whitebark pines lack most chemical defenses
Rely on cold
Target larger trees
More cambium for larvae
Invasive Eurasian blister rust
Fungi
Introduced in 1900
Kills all sizes of whitebark pine
Makes trees more susceptible to beetles
Decreases their resin
The combination creates ghost forests
Grizzly connection
< 1% of the former range
Whitebark pine only mast every 3-5 years
Grizzly bears need large areas of trees
Decrease in cutthroat trout
Whirling disease?
Causes odd bony growths
Invasive trout
Decreasing winter-killed elk and bison
Increasing predation on elk calves
Wolves, Elk, and Aspen
Functional extinct since 1929
Protected in 1973 by the Endangered Species Act
Predator control was questioned in the 1930s
1960s too many elk
19,000- 6,000
Willow and aspens increase
Wolf behavior modification is just a hypothesis, not confirmed
Very little effect in winter
Willow is noticeably taller in many places
Not all
Elk kill all willow → beavers die from lack of willow → water table lowers from lack of dams → willows can’t regenerate → beavers can’t recover
Wolves and pronghorn
Increase in wolves → Decrease in coyotes → increased fawn survival
The greatest biodiversity exists on the private lands of low-elevation