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Climate change impacts and forest management

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<strong>Climate</strong> <strong>change</strong><br />

<strong>impacts</strong> <strong>and</strong> <strong>forest</strong><br />

<strong>management</strong><br />

Jana Albers, DNR


<strong>Climate</strong> <strong>change</strong> in the past<br />

Anticipated climate <strong>change</strong>s for Mn<br />

Adding other <strong>forest</strong> health stressors<br />

“Houston, we have a problem.”<br />

Forest <strong>management</strong> adapts


<strong>Climate</strong> <strong>change</strong> in the past<br />

• Four <strong>forest</strong>ed provinces<br />

made up of many types of<br />

<strong>forest</strong> communities at the<br />

present time.<br />

• Forested communities are<br />

literally “living on the edge” of<br />

the prairie.<br />

• The configuration of <strong>forest</strong><br />

<strong>and</strong> prairie/<strong>forest</strong> border was<br />

not always like this.


Evidence of climate <strong>change</strong> in the past<br />

Sequence of major vegetation types in MN from 11,000 years ago to the present.


• Forest communities are<br />

reshaping themselves all<br />

the time.<br />

• Even very “recent”<br />

movements of tree<br />

species show evidence of<br />

a changing climate.<br />

Duration of pine <strong>forest</strong>s in MN<br />

Pollen records show years of<br />

continual occupancy of pine<br />

communities from the present<br />

looking backwards to the last<br />

glaciation.<br />

Almendinger, 2003


Anticipated climate <strong>change</strong>s for Mn<br />

• Increased levels of CO2 <strong>and</strong> O3 in atmosphere.<br />

• Warming temperatures.<br />

In winter, minimum temps will be warmer.<br />

Growing season will be longer.<br />

• Drier weather during the growing season.<br />

• Relative humidity peaks higher in summer.<br />

• More wind storms <strong>and</strong> thunderstorms.<br />

More large-scale blow-down events.<br />

Less percolation of rain water into soil.<br />

Lee Frelich, U Mn


Possible <strong>change</strong>s to growing conditions: 2095<br />

<strong>Climate</strong> projections<br />

for high emission<br />

scenario by 2095.<br />

Union of Concerned Scientists.


Future climate<br />

analogs for Mn<br />

l<strong>and</strong>scapes 50<br />

years into the<br />

future<br />

Galatowitsch, 2009


A schematic depicting the possible dynamics of climate <strong>change</strong><br />

Impacts on<br />

<strong>forest</strong>s<br />

Frelich & Reich, 2009


Tree species maladapted to the future climate will experience<br />

decreases in abundance <strong>and</strong> distribution. Other species will<br />

benefit from climate <strong>change</strong>. Some may be neutral.<br />

The USFS has developed the Tree<br />

Atlas showing where climate<br />

<strong>change</strong> is likely to have effects for<br />

the 130+ tree species in the NE<br />

USA. Based on FIA plots.<br />

In MN, 12 of 22 <strong>forest</strong> species will<br />

have hotspots of <strong>change</strong> where<br />

the tree populations are likely to<br />

diminish. Iverson, 2007<br />

White spruce<br />

Hotspots are hatched polygons.<br />

http://www.nrs.fs.fed.us/atlas/tree/tree_atlas.html


Evidence of tree migration<br />

• Using FIA data, researchers<br />

found that 11 of 15 northern<br />

tree species are moving<br />

northwards, from 20 to 100<br />

km/ century. Woodall, 2009<br />

Fast paced: basswood, s maple, yel<br />

birch, n r oak, bl ash <strong>and</strong> bt aspen<br />

Slow paced: tam, r pine, w pine <strong>and</strong><br />

nw cedar,<br />

Static: balsam fir, bl spruce, w pine,<br />

q aspen BAM <strong>and</strong> p birch<br />

Based on the centers of tree biomass<br />

(red) <strong>and</strong> seedling abundance (blue) for<br />

each tree species.<br />

Tree biomass<br />

Seedling counts<br />

Note: The estimated speed of tree<br />

migration in post-glacial times was<br />

50 km/ century.<br />

Based on comparison of where trees<br />

<strong>and</strong> seedlings at each latitude class.


Implications for tree species<br />

• The prairie/ <strong>forest</strong> border will shift<br />

north <strong>and</strong> east.<br />

• The range of boreal species will shift<br />

northeast.<br />

• Red <strong>and</strong> white pines will hold their<br />

own or do better.<br />

• Northern hardwoods will exp<strong>and</strong>. Red<br />

maple will become very<br />

abundant. Sugar maple <strong>and</strong> red<br />

oaks will increase.<br />

• Birch will rapidly decline; aspen may<br />

slowly decline.<br />

• Central hardwoods will increase but<br />

need connectivity.<br />

Iverson, Frelich, White<br />

Lose acreage:<br />

Quaking aspen<br />

Paper birch<br />

Balsam fir<br />

Black ash<br />

Black spruce<br />

Balm of gilead<br />

Tamarack<br />

Jack pine<br />

White cedar<br />

Mt. maple<br />

Gain acreage:<br />

Bur oak<br />

E. red cedar<br />

Cottonwood<br />

Black walnut<br />

Hackberry<br />

N. red oak<br />

White oak<br />

Honey locust<br />

Silver maple<br />

Boxelder


<strong>Climate</strong> <strong>change</strong> is likely to reinforce the deleterious effects<br />

of other <strong>forest</strong> organisms <strong>and</strong> processes<br />

?<br />

Frelich & Reich, 2009


Effects of deer <strong>and</strong> earthworms will be accelerated by climate <strong>change</strong>.<br />

Deer, with populations 2 to 20 times<br />

higher than historical levels, browse<br />

on herbs <strong>and</strong> tree seedlings.<br />

Currently, they cause the loss of<br />

48-81% of native plant species.<br />

Rooney, 2011<br />

Earthworms consume the duff which<br />

leads to exposed soil, soil<br />

compaction, runoff, droughtier soils,<br />

<strong>change</strong>d nutrient cycles <strong>and</strong> likely<br />

incursion of invasive plants.<br />

Where deer <strong>and</strong> worms occur<br />

together, they cause a major<br />

transformation of the <strong>forest</strong>.<br />

Frelich, 2011


Exotic, invasive plants:<br />

• Their effects will be on a species-by-species basis<br />

affecting biodiversity, shading, nutrient cycling, etc.<br />

• As climate <strong>change</strong> heats up, likely to see:<br />

establishment of more inv plant species,<br />

altered range/distribution of these plants,<br />

altered effectiveness of control strategies.<br />

• Their effects will reinforce warming <strong>impacts</strong>.


Wildfires: <strong>Climate</strong> <strong>change</strong> will likely create<br />

a fire-prone environment with more fuels<br />

<strong>and</strong> more lightning strikes.<br />

• On average, 14% of all st<strong>and</strong>ing<br />

trees are dead (snags). NRS 2008<br />

• With anticipated <strong>impacts</strong> of climate<br />

<strong>change</strong>, the number of snags is likely<br />

to increase, fueling future wildfires.


Blowdown:<br />

• More frequent <strong>and</strong> more serious<br />

storms (derechos) in northern MN<br />

are expected.<br />

• In the last 20 years, we’ve<br />

exceeded a millenium’s worth of<br />

blowdown acres in MN.<br />

Almendinger


Insects <strong>and</strong> pathogens (native <strong>and</strong> exotic):<br />

Even a modest climate <strong>change</strong> will have rapid<br />

<strong>impacts</strong> on the distribution <strong>and</strong> abundance of<br />

many <strong>forest</strong> insects <strong>and</strong> pathogens because of their<br />

short life cycles, mobility, reproductive potential<br />

<strong>and</strong> physiological sensitivity to temperature.<br />

Ayres, 2007<br />

<strong>Climate</strong> <strong>change</strong> could<br />

• Directly affect the development <strong>and</strong> survival<br />

of insects <strong>and</strong> pathogens.<br />

• Alter the abundance of their natural enemies<br />

<strong>and</strong> competitors.<br />

• Alter host tree physiology or defenses.


Examples of <strong>impacts</strong> of climate <strong>change</strong> on insects<br />

• Reduced overwintering mortality from cold weather events.<br />

• Faster development/ more generations per season due to<br />

warmer <strong>and</strong> longer summers.<br />

Ips pine bark beetles could move from<br />

2 generations per year to 3 gens/yr.<br />

in central <strong>and</strong> northern MN.<br />

• Disrupt the phenological synchrony between insects <strong>and</strong> their<br />

natural enemies.<br />

Population increases of larch casebearer are<br />

thought to be caused by warmer temperatures<br />

that favor the defoliator over its parasites.


Examples of <strong>impacts</strong> of climate <strong>change</strong> on insects<br />

Insects <strong>and</strong> pathogens may<br />

move/migrate <strong>and</strong> establish<br />

new ranges as climate<br />

becomes warmer<br />

• As the mountain pine<br />

beetles become<br />

established in boreal<br />

jack pines, they might<br />

move east through<br />

Canada, into<br />

Minnesota.<br />

• 2°C rise allows<br />

expansion about 360<br />

miles north.<br />

Current<br />

locations of<br />

mountain<br />

pine<br />

beetles<br />

Jack pine<br />

Mountain pine beetle


Changed tree physiology <strong>and</strong> defenses:<br />

As trees become stressed by drought, <strong>change</strong>s in tree chemistry<br />

can occur. Certain pests, called “opportunistic pests”, key in on<br />

these stress-related chemicals <strong>and</strong> successfully attack <strong>and</strong> kill the<br />

stressed trees.<br />

Stressed<br />

trees<br />

Energy<br />

depletion<br />

Site, Age,<br />

Defoliation,<br />

Drought,<br />

Wound,<br />

Construction<br />

+<br />

Opportunistic<br />

Phloem miners<br />

pests<br />

Armillaria<br />

Dead trees


Examples of tree species that have opportunistic pests<br />

• Pines, tamarack,<br />

oaks, birches,<br />

aspen, etc.<br />

• Armillaria root<br />

disease can kill<br />

stressed trees.<br />

Red pine<br />

Bark beetles<br />

• Persistent<br />

outbreaks of<br />

opportunists<br />

will be the<br />

bellwethers of<br />

climate <strong>change</strong>.<br />

Northern red oak<br />

Two-lined chestnut borers<br />

http://www.nrs.fs.fed.us/atlas/tree/tree_atlas.html


Multiple agents will reinforce<br />

the impact of global warming<br />

on <strong>forest</strong>s.<br />

• In the short-term, weather<br />

<strong>change</strong>s will allow<br />

opportunistic pests <strong>and</strong><br />

abiotic declines to accelerate<br />

the demise of tree species no<br />

longer suited to their current<br />

sites. They will lose<br />

abundance <strong>and</strong> acreage.<br />

• Other tree species will<br />

migrate into MN or existing<br />

species will become more<br />

prevalent as their range<br />

exp<strong>and</strong>s. They will gain<br />

abundance <strong>and</strong> acreage.<br />

Implications of climate <strong>change</strong><br />

Lose acreage:<br />

Quaking aspen<br />

Paper birch<br />

Balsam fir<br />

Black ash<br />

Black spruce<br />

Balm of gilead<br />

Tamarack<br />

Gain acreage:<br />

Jack pine<br />

Bur oak<br />

White cedar<br />

E. red cedar<br />

Mt. maple<br />

Cottonwood<br />

Black walnut<br />

Hackberry<br />

N. red oak<br />

White oak<br />

Honey locust<br />

Silver maple<br />

Boxelder


“Houston, we have a problem.”<br />

Expectations: Forests are being viewed as essential for climate<br />

<strong>change</strong> mitigation via carbon sequestration <strong>and</strong> biomass production<br />

on a global scale.<br />

Fears: Will there be so many deleterious <strong>change</strong>s to <strong>forest</strong>s in a very<br />

short time that <strong>forest</strong>s cannot sustain themselves?<br />

Human abilities <strong>and</strong> capacities: What about <strong>forest</strong> <strong>management</strong>?<br />

Are old goals <strong>and</strong> schemes irrelevant? How do we “hit” multiple<br />

moving targets involved with climate <strong>change</strong>? When <strong>and</strong> where do<br />

we start?


Forest <strong>management</strong> adapts<br />

• Continue to use existing <strong>and</strong> proven <strong>management</strong> techniques.<br />

These keep our trees <strong>and</strong> native plant communities vigorous,<br />

productive <strong>and</strong> resilient to adverse <strong>change</strong>s.<br />

D’Amato<br />

• Just like the trees in the <strong>forest</strong> adapting to the effects of climate<br />

<strong>change</strong>, <strong>forest</strong>ers must adapt <strong>management</strong> strategies to new <strong>and</strong><br />

anticipated conditions.<br />

<strong>Climate</strong> <strong>change</strong> <strong>and</strong> <strong>forest</strong>s<br />

of the future: Managing in<br />

the face of uncertainty.<br />

Millar, Stephenson <strong>and</strong> Stephens


Adaptation strategies defined<br />

Millar, Frelich, D’Amato, DNR, etc<br />

Resistance = help species/ecosystems<br />

to remain un<strong>change</strong>d in the face of<br />

climate <strong>change</strong>.<br />

Resilience = increase the abilities of<br />

species/ecosystems to absorb or adapt<br />

to effects of climate <strong>change</strong>.<br />

Facilitation = actively manage to help<br />

the ecosystem adapt toward a<br />

predicted direction of climate <strong>change</strong>.


Resistance = defend high-risk or high-value resources<br />

against <strong>change</strong>. “Homel<strong>and</strong> security approach”<br />

• Costly; direct at critically endangered<br />

resources; effective for a short time.<br />

• More effective now rather than later.<br />

• Allows NP Communities to persist until<br />

other adaptations become necessary.<br />

• Prevent or reduce other external <strong>forest</strong><br />

health stressors: deer, invasive pests,<br />

invasive plants, earthworms.<br />

• Limit size of wildfires; create fire breaks.<br />

• Use thinning to control st<strong>and</strong> density so<br />

trees can survive drought.<br />

• Use ERF to buildup stored “carbon”.


Resilience = increase the abilities of species/ ecosystems to<br />

absorb or adapt to effects of climate <strong>change</strong> by<br />

building st<strong>and</strong> <strong>and</strong> ecosystem complexity.<br />

“Health care approach”<br />

• Will work as an interim measure or<br />

where uncertainty is high.<br />

• Increase species diversity.<br />

• Increase age diversity.<br />

• Increase genetic diversity by<br />

planting “southern” seed<br />

sources.<br />

• Move towards uneven-aged mgt. or<br />

multi-age st<strong>and</strong>s.<br />

• Prevent or reduce external stressors.<br />

• Preserve buffers around reserves.<br />

• Build the up the seed bank.<br />

Seed<br />

zones


Facilitation = actively manage to help the ecosystem adapt<br />

towards a predicted direction of climate <strong>change</strong>.<br />

“Humble helper approach”<br />

• We have limited capacity to underst<strong>and</strong> it all.<br />

• Will work for the largest magnitudes of climate<br />

<strong>change</strong>.<br />

• Risky to implement now because we aren’t<br />

sure how climate <strong>change</strong> will actually proceed.<br />

• Establish travel corridors in expected direction<br />

of species <strong>change</strong>/ migration.<br />

• Establish transitional refugia.<br />

• Assisted migration <strong>and</strong> colonization of species<br />

esp. oaks <strong>and</strong> other large-seeded trees.<br />

• Anticipate <strong>and</strong> plan for the risks & losses:<br />

large-scale fires, pest outbreaks, declines, etc.<br />

• Continue to prevent or reduce <strong>impacts</strong> of nonclimate<br />

tree stressors.


Continue to use existing <strong>and</strong> proven <strong>management</strong> techniques.<br />

These keep our trees <strong>and</strong> native plant communities vigorous,<br />

productive <strong>and</strong> resilient to adverse <strong>change</strong>s.<br />

Build in “response diversity”. Manage for high tree species<br />

diversity at the st<strong>and</strong> <strong>and</strong> l<strong>and</strong>scape level so that another species<br />

can fill the vacated niche of species that disappears.<br />

D’Amato<br />

• Build structural complexity:<br />

Promote age class diversity;<br />

at least 2 age classes.<br />

Increase reliance on uneven-aged<br />

<strong>management</strong>.<br />

• Build compositional complexity:<br />

Use new species mixes.<br />

Increase species redundancy by<br />

introducing species over a<br />

wide range of environments.


• Trees <strong>and</strong> their <strong>forest</strong> communities<br />

have survived large-scale tree migration<br />

events in the past <strong>and</strong> <strong>change</strong>s in the<br />

location of the prairie/ <strong>forest</strong> border.<br />

• I believe that new <strong>forest</strong> communities<br />

will emerge along with new disturbance<br />

regimes that will maintain them.


Any questions?


DNR Forest Health Unit<br />

Val Cervenka<br />

FH Coordinator<br />

651 259-5296<br />

Susan Burks<br />

Invasive Spp Coord.<br />

651-259-5251<br />

Jana Albers<br />

NW FH Spec.<br />

218 327-4234<br />

Mike Albers<br />

NE FH Spec.<br />

218 327-4115<br />

Ryan Blaedow<br />

Central FH Spec.<br />

651-259-5821


Feedback on<br />

results of<br />

adaptive<br />

<strong>management</strong><br />

strategies will be<br />

provided by<br />

monitoring.


Examples of maladapted trees experiencing stress from<br />

abiotic factors<br />

• Adverse environmental factors add up to cause vigor<br />

problems.<br />

• No pests involved, at least, initially.<br />

• Trees with existing declines may be that much more<br />

vulnerable to the effects of climate <strong>change</strong>.<br />

Birch decline<br />

Ash decline<br />

Paper birch<br />

Black ash


A. Because most <strong>forest</strong> pests are sensitive<br />

to temperature, even modest warming<br />

could speed up their metabolism<br />

requiring more food,<br />

increasing mobility & distribution,<br />

increasing reproduction.<br />

B. Deer, invasive plants <strong>and</strong> earthworms<br />

cause damage to native flora, soil<br />

structure <strong>and</strong> nutrient cycling. Their<br />

effects by will be accelerated.<br />

C. Trees maladapted to their existing sites<br />

will become more <strong>and</strong> more drought<br />

stressed. Conversely, some species will<br />

benefit, by gaining abundance <strong>and</strong>/or<br />

distribution. Others may be unaffected.

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