Forest Ecology

Forest Ecology
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Forest Ecology Forest Ecology An Evidence-Based Approach Forest ecology is the science that deals with everything in forests, including plants and animals (and their interactions), the features of the environment that affect plants and animals, and the interactions of humans and forests. All of these components of forests interact across scales of space and time. Some interactions are constrained, deterministic, and predictable; but most are indeterminant, contingent, and only broadly predictable. Forest Ecology: An Evidence-Based Approach examines the features common to all forests, and those unique cases that illustrate the importance of site-specific factors in determining the structure, function, and future of a forest. The author emphasizes the role of evidence in forest ecology, because appealing, simple stories often lead to misunderstandings about how forests work. A reliance on evidence is central to distinguishing between appealing stories and stories that actually fit real forests. The evidence-based approach emphasizes the importance of real-world, observable science in forests. Classical approaches to ecology in the twentieth century often over-emphasized appealing concepts that were not sufficiently based on real forests. The vast amount of information now available on forests allows a more complete coverage of forest ecology that relies on a strong, empirical foundation. Forest Ecology: An Evidence-Based Approach is the ideal companion text for the teaching of upper-level undergraduate and graduate courses in forest ecology.

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Dan Binkley. Forest Ecology

Table of Contents

List of Illustrations

Guide

Pages

Forest Ecology. An Evidence‐Based Approach

Preface. How Do We Come to Understand Forests?

How Confident Should You Be?

All Forest Ecology Fits Into a Framework and a Method

A Picture May Be Worth 1000 Words, But a Graph Can Be Worth Even More

The Most Important Points to Understand from Figures B and C Are Not About Precipitation or Temperature

Confidence Bands Around Trends Come in Two Types

The Stories in This Book Have Two Pieces, Told in Three Ways

Forests Are Complex Systems That Are Not Tightly Determined

Acknowledgements

CHAPTER 1 The Nature of Forests

Forest Ecology Deals with Individual Trees Across Time

Many Processes Occur in a Tree Every Hour

Tree Physiology Follows Daily Cycles

Trees Must Cope with Seasonal Cycles Through Each Year

Trees Grow and Reproduce at Times Scales of a Century

The Story of Forests Is More than the Sum of the Individual Trees, Because Interactions Are So Strong

The Coweeta Forests Aren't the Same as Two Centuries Ago

Across Dozens of Generations of Trees, Almost Everything Changed at Coweeta

The Futures of the Tree and the Forest Will Depend on Both Gradual, Predictable Changes and Contingent Events

Ecological Afterthoughts: Is a Forest an Organism?

CHAPTER 2 Forest Environments

Climate Influences Where Forest Occur, and How They Grow

Warmer Forests Have More Species of Trees

Chemical and Biological Reactions Go Faster with Increasing Temperature

Temperature is the Balance Point Between Energy Gains and Losses

All Objects Shine; Hot Objects Shine Brightly

Incoming Sunlight Decreases in Winter and at Higher Latitudes

Forests Receive Shortwave Sunlight, and Shine off Longwave Radiation

Temperatures Decline with Increasing Latitude

Temperatures Increase at Lower Elevations

Temperature Variation Over Time, and Across Space, Strongly Influences Forest Ecology

Temperature Strongly Influences Phenology and Growth

Forests Use Very Large Amounts of Water

Water Flows Down Gradients of Potential, Which Sometimes Means Going Up

Wind Shapes Trees and Forests

Events and Interactions Are More Important Than Averages and Single Factors

Fires Depend on Temperature, Water, Winds

Droughts Affect Trees, Beetles, Forest Structure and Fire Intensity

Weather Events Can Matter More than Averages

Ecological Afterthoughts

CHAPTER 3 Evolution and Adaptation in Forests. What's in a Name?

The Core Idea of Evolution Is the Combination of Variation, Failure, and Innovation

Darwin Could Not Explain Why Variations Occurred, or Why They Were Passed on to Offspring

Does Selection Work on Species or on Genes, or Is This Only a Chicken‐and‐Egg Question?

Biology Operates from a Simple Story of DNA to Incredible Complexity of Proteins and Biochemistry

Why Are There Only Two Species of Tulip Poplar, and Why Are They 12 000 km Apart?

Tall Growth Requires Strong Stems

The First Trees from Seeds Were Gymnosperms

Collaboration with Insects Helped Angiosperms Take over the Planet

The Highest Diversity Is in Tropical Rain Forests

Do all Trees Need to Have Trunks?

Some Broadleaved Trees Make Fertilizer Out of Thin Air

What's the Largest Tree in the World?

History Has No Need to Repeat Itself

Critchfield Spruce Melted Away at the End of the Last Ice Age

Ponderosa Pine Went from Obscurity to Prominence in Just a Few Thousand Years

Eastern Hemlock Has Had a Dynamic History of Up and Down

Almost all the Animal Species Are Missing from Temperate and Boreal Forests

Climate, Animals and Fire Interact Across Forest Generations

Modern Forests Are Changing Faster Than Ever, on a Global Scale

Ecological Afterthoughts

CHAPTER 4 Physiology and Life History of Trees

Biological Energy Is About Moving Electrons

Forest Energy Comes from Sunlight; Wood Comes from Thin Air

Why Are Leaves Green?

Leaves Are Not Always Green

Carbon Uptake Is the Second Half of Photosynthesis

Growth Happens After Photosynthesis – Sometimes Long After

Trees Do Not Live by Carbon Alone

Photosynthesis and Growth Depend on Acquisition of Resources

More Leaves Means More Light Capture, up to a Point

One Square‐Meter of Leaves Has a Mass of 50–150 g

Each Square Meter of a Forest has Multiple Layers of Leaves above

Large Trees Depend on Large Roots

Networks of Fine Roots Permeate Soils

Do Roots Take Up Water and Nutrients?

Trees (and Mycorrhizal Fungi) Obtain Nutrients by the Interaction of Mass Flow and Diffusion

Life History Is the Story of Going from Seed to Mature Seed‐Producing Tree

Tree Seeds Range in Mass from Smaller than a Flea to Larger than a Mouse

Why Is the Understory of a Forest a Tough Place for Small Trees to Thrive?

All Good Summers Come to an End

Most Trees Die Young

Reproduction Is the Beginning and the End of Life History Stories

Ecological Afterthoughts: What Benefit Comes from Aspen Having Chlorophyll in Its Bark?

CHAPTER 5 Ecology of Wildlife in Forests

Many Species of Trees Coevolved with Animals as Seed Dispersers

Some Animal Species Specialize in Eating Trees

Livestock Grazing and Browsing has been a Core Part of People’s Livelihoods Through History

Was Aldo Leopold Right About the Kaibab Deer Herd?

Wildlife Population Dynamics Occur Within Complex Ecological Systems

Moose and Wolves Established New Populations on Isle Royale in the Early 1900s

The Cycles of Snowshoe Hares and Lynx Repeat, but They Are Far from Simple

Patterns and Processes of Wildlife Population Dynamic Shift Across Space and Time

Good Ideas Without Good Evidence May Be Unreliable, or Wrong

Strong Evidence Comes from Comparisons of Treatments at the Same Point in Time

Ecological Afterthoughts

CHAPTER 6 Forest Soils, Nutrient Cycling, and Hydrology

Forests Need Soils for Physical Support

Soils Here Are Different from Over There, and Soils Now Are Different from Soils Then

Organic Matter is the Top Feature of Soils

Clay Content Comes in Second to Organic Matter

Soils Breathe

The Variety of Soils Is Parsed into Soil Taxonomic Groups

Soils Differ in Age, Even if Most Don't Have Birthdays

Trees Affect Soils

Decomposition Reverses Photosynthesis and Nutrient Uptake

Almost all Forest Biodiversity Is Found in the Soil

Leonardo da Vinci Couldn't Figure out How Water Got to the Top of Mountains

The Atmosphere Holds Only a Few Days of Precipitation

Forest Water Budgets Begin with Precipitation

Water Use by Forests Can Be Measured Across a Range of Scales

Trees Use Most (or All) of the Water

George Perkins Marsh (and Everyone Else) Was Wrong About the Effect of Forest Cutting on Water

Reliable Generalizations Require Evidence from More than One Case

Nutrients Make Life Possible

Nutrients Come From the Atmosphere and From Rocks

Biogeochemical Cycles Are Complex

Decomposition is the Centerpiece of Nutrient Cycling in Forests

Nutrient Losses Are Chronic and Episodic

Ecological Afterthoughts: Consequences of a Warmer World for Snow, Streams, and Forests

CHAPTER 7 Ecology of Growth of Trees and Forests

Forests Are Small and Large, and Growth Is the Key Process Driving Increases

Growth is Examined in a Variety of Ways

Yield Tables Were an Early Example of Parsing Variation in Forests Across Landscapes

Patterns in Yield Tables Were Explained Based on “Growing Space”

Production Ecology Parses Growth into Ecophysiological Factors Constrained by Mass Balance

Forest Growth Is a Function of Resources in the Environment, Resources Acquired, and Efficiency of Resource Use

The Growth of a Forest is the Sum of the Growth of All the Trees

Large Trees Usually Grow Faster than Small Trees in the Same Forest

Dense Forests Have the Highest Growth Rates

Forest Growth Peaks at a Young Age and Then Declines, but Not the Growth of the Biggest Trees in the Forest

Forest Growth Changes over Time, Not Just with Age

Neighbors Influence the Growth of Trees

How Might a Mixed‐Species Forest Grow Faster than a Single‐Species Forest?

Mixed‐Species Forests Usually Cannot Match the Growth of Fast‐Growing Monocultures

When a Species Increases Resource Supplies, Mixtures May (or May Not) Outperform Single‐Species Forests

The Growth of Mixed‐Species Forests Changes over Time

Mixed‐Species Forests Are not Only About Growth Interactions Between Species

Understory Vegetation is Important in Most Forests

Mortality Gets the Final Word on Forest Production

Death is Not the End of the Story for Trees

Ecological Afterthoughts: Is it Better to Remove Small Trees or Large Trees When Thinning a Forest?

CHAPTER 8 Forests Across Space. The Three Most Important Things for a Tree Are Location, Location, and Location

How Small Can a Forest Be?

Forests May Be Divided Into Stands, But Not All Forests Are Structured As Distinct Stands

People Engage with Forests by Defining Areas of Interest

Larger Plots Contain More Species

Vegetation Differs Between Locations

Space Has Another Dimension for Animals

Differences in Forests Usually Increase with Distance, But Not Always

Location Matters Both Locally and Regionally

Resource Use Varies Across Landscape Gradients

Mind the Gap: Spatial Patterns of Trees Within Forests Modify Resource Supplies

The Ecology of Gaps is Not Binary

The Ecology of Gaps and Edges Affects Animals, and Is Shaped by Animals

The Location of Each Tree Allows a Wide Range of Assessments of Forest Structure and Processes

Forest‐Level Information Can Be Dissected Down to the Level of Individual Trees

Riparian Forests Are Special and Important, for Different Reasons in Different Forests

Spatial Patterns Are Important, Even in the Most Uniform Forests

Forest Classification Is Different in the Twenty‐First Century

Ecological Afterthoughts: When It's Not About the Trees

CHAPTER 9 Forests Through Time

Sometimes a Classic Story Comes True

Long‐Term Experimental Forests Provide Knowledge at the Scale of Tree Lifetimes

When Recorded History Is Not Enough, Tree Rings Can Provide a Record of Both Age and Size

Dendrochronology Developed Because There Are No Canals on Mars

Dendrochronology Can Explain Past Forest Structure and Dynamics

Darwin's Ideas Contributed Very Little to Early Ideas of Forest Change (Unfortunately)

Chronosequences Are a Shortcut to the Future, But They May Be Unreliable

Strong Chronosequences Require Large Numbers of Replicates

Growth Always Declines in Old Forests

People Change How Forests Change Over Time

Time Scales of Forests and Human Planning Do Not Always Match

Over the Long‐Term, Forests Have Not Changed As Predicted

Ecological Afterthoughts

CHAPTER 10 Events in Forests: Wind, Insects and Diseases

It's Remarkable That Trees Can Stand Up to Strong Winds

Tree Stems May Break or Uproot

Storms Blow in with a Wide Range of Wind Speeds

Storm Impacts Can Be Severe in Local Areas

Storms that Are Severe Enough to Be Named Are Strong Enough to Topple Vast Numbers of Trees

How Large an Area Can Be Covered by a Single Storm?

How Massive Can a Storm's Impact Be?

When Will the Next Storm Come?

The Next Storm Will Be Different Than the Last One

Trees Provide the Dominant Structure of Forests, But Small Insects Can Play a Very Major Role

How Do Tiny Insects Manage to Kill Large Trees?

Which Trees Are Most Vulnerable to Mountain Pine Beetles?

Which Forests Are Most Susceptible to Mountain Pine Beetles?

Mountain Pine Beetle Impacts Are Consistent When Scaled Up to Regional Areas

Tree Death Alters Environmental Conditions at Local Scales, But Less at Watershed Scales

Why Don't Beetles Kill More Trees?

Is This a Healthy Forest?

Forests Often Thrive When Insects Kill Trees

Should Forests with Lots of Beetle‐Killed Trees Be Logged?

Other Dynamics of Forests and Beetles Occurred Across the Region Too

Other Forests and Other Insects Have Other Stories

Tree Diseases Are Reshaping Forests in a Globalized World

Major Events May, or May Not, Influence the Probability of Other Major Events

Events in Combinations Can Have Drastically Different Legacies

Ecological Afterthought: The Ecology of Avalanches

CHAPTER 11 Events in Forests: Fire. Forest Growth Sets the Stage for Rapid Return to Chemical Equilibrium

Thick Bark Protects Cambium from Heat

The Post‐Fire Forest May Be Dominated by Resprouting Vegetation

Post‐Fire Environments Can Be Good for Seedling Establishment

The Spatial Scale of Forest Fires is Important, But Not Simple

Most Forest Fires Are Small, Though the Uncommon Large Fires Have Great Impacts

Fires Burn Differently at Different Places

Periods of Gradual Change Are Punctuated by the Large Changes from Fire Events

Typical Fire‐Free Periods Within Forest Types Vary Across Sites and Over Centuries

When Fire‐Free Intervals Get Longer, Forests Get Denser

The Spatial Aspects of Fires Also Include Patterns Within Burned Patches

Fire Ecology Might, or Might Not, Be Described with Fire Regimes

Fires Change Soils

Fires Generate Erosion in Areas That Burn, with Sediment Deposition Downslope

Erosion After Fire is Usually Not a Problem, But Sometimes It's Very Severe

Each Species of Animal Has a Different Response to Forest Fires

Fires Interact with Other Major Events in Forests

Ecological Afterthoughts: How Do Slow Changes in Forests Shape the Effects of Fires?

CHAPTER 12 Events in Forests: Management

Harvesting Is the Third Largest Forest Event Across the Planet

Few Forests Are Plantations, But Plantations Provide Most of Our Wood

Deforestation Can Be Tallied from Government Reports, or from Satellites

Human Influences on Forests Have a Spectrum from Low to Very High

Tree Farms Are All About Production, Not Broader Ecological Features

How Sustainable Are Tree Farms?

Managed Forests Come in a Variety of Systems

Rotational Forests Have Birthdays

Understories and Overstories Interact Through a Rotation

Continuous Cover Forests Have no Birthdays, and Less Change

Tree Growth Is Faster in Rotational Forestry than in Continuous Cover Forestry

Management of Unmanaged Forests May Seem Like an Oxymoron

How Does Retaining Trees Influence the Next Forest After Logging in Unmanaged Forests?

Harvesting Is the End of the Line for Some Trees and Forests, and the Beginning of the Next Forest

Harvesting Is Not the Only Big Event that Happens in Managed Forests

Can Forests Remove Enough CO2 from the Atmosphere to Save the Planet?

Ecological Afterthoughts: What's Next for These Forests?

CHAPTER 13 Conservation, Sustainability and Restoration of Forests

Conservation, Sustainability and Restoration Build Values, Ethics, and Esthetics onto a Foundation of Forest Ecology

Conservation, Sustainability and Restoration Are About the Future

Why Do Species Go Extinct, and How Can This Be Prevented?

Conserving Old Forests Is Important, but Old Forests Do Not Last Forever

Conservation and Sustainability Have Similarities

Restoration Comes into Play When Conservation and Sustainability Have Not Been Achieved

The History of a Forest Might Be Read in Reports, in Photographs, in Trees and Remnants of Trees

Clues to the Past Structure of Forests Lurks in Tree Rings, Stumps, and Logs

What Does It Take to Restore a Forest?

Many Forests Have Reestablished Following Agricultural Land Use

Forest Reestablishment May Be Faster with Planting, and Contain More Desirable Species

Forest Reestablishment Leads to the Redevelopment of Forest Soils

Reestablishing Forests in the Absence of Soils Is a Major Challenge, Requiring Insights and Money

Management Can Shift Forests Away from Undesirable Conditions

Two Key Ideas Connect Forest Ecology with Conservation, Sustainability, and Restoration

Ecological Afterthoughts: Restoring Forests May Be About Restoring Non‐Tree Vegetation

CHAPTER 14 Forests of the Future

Forests Have Already Changed, and Continue to Change

Can Invasions Be Predicted?

Some Forests Are More Invasible Than Others

Not all Invasive Species Are Alike: Identity Matters

Plantations of Non‐Native Trees Can Lead to Invasions

Biological Control May Help Limit Invasive Species

Genetics Matter

The Future Is Certain to Be Warmer, with More CO2 in the Atmosphere

If Droughts Increase, Which Forests and Trees Will Show Increased Mortality?

Changing Climates Will Change the Distribution of Species

Fires Have Always Been Important in Forests, and Fires May Become More Important

People Will Contribute to Shaping Future Forests

All These Factors Will Interact to Shape the Dynamics of Future Forests

Rocket Science Can Get You to the Moon, but Pocket Science Leads to Better Outcomes in Forests

The Core Framework Actually Needs a Fourth Question

Ecological Afterthoughts: Growing Meaning in Forests

References

Index. A

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DAN BINKLEY

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Continuing back to 12 500 years ago, the continent (and much of the globe) was undergoing rapid warming as the most recent Ice Age ended. Temperatures in the Coweeta Basin would have risen by more than 5 °C from conditions that prevailed for 100 000 years. Under colder conditions, the forests in the Basin would have resembled forests that are currently found farther north, with pines and spruces dominating even the lower elevations. During some periods, the assemblages of trees species across the region included combinations that have no modern analog in local forests, or in forests now found farther north (Jackson and Williams 2004). Assemblages of tree species change in response to interactions among temperature, precipitation, and biotic factors. Unlike organisms, the genotypes of forests change routinely as species come and go.

The most notable difference in the forest at the end of the Ice Age would have been the presence of many large species of mammals in the region. The list of now‐extinct species includes tree‐browsing American mastodons; grass and tree‐browsing Columbian mammoths; woody‐plant browsing stag moose; tree‐eating giant beavers more than 2 m in length; and large predators such as dire wolves, sabretooth cats, and massive short‐faced bears. The now‐extinct mammals would have been joined by at least one now‐extinct tree species, Critchfield spruce (Jackson and Weng 1999).

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