Community dynamics in old growth and second growth hemlock forests.

Slides:



Advertisements
Similar presentations
Population Ecology.
Advertisements

SUCCESSION AND STABILITY
Dendroecology of the dwarf shrub Dryas integrifolia M. Vahl. near Churchill, Manitoba By Robert Au Supervisor: Jacques Tardif Committee Members: G. Scott.
The Hemlock Crisis in Georgia (and the eastern U.S.) James Johnson Forest Health Coordinator Georgia Forestry Commission This we know: the earth does not.
Methods Tree selection varied slightly at the four different locations. On the rim and river trails, I walked along established paths and selected the.
Hemlock woolly adelgid resistance E. Preisser, B. Maynard, R
Height to DBH Ratio in N. Olympic Forests Karsten Turrey, North Olympic Peninsula Skills Center Natural Resources Prior Knowledge I know that as trees.
Estimated biomass and carbon committed to decomposition in a north Georgia 2011 tornado swath Chris J. Peterson 1, Jeffery B. Cannon 2, and Luke J. Snyder.
COMMUNITY ECOLOGY I: BIODIVERSITY Community: Any assemblage of populations [of plants and/or animals] in a given area or habitat.
Geographic Distributions of Plant Diversity in the Southeastern US Aaron Moody, Bob Peet, Todd Jobe, Jen Costanza, Dahl Winters, Matt Simon NASA Biodiversity.
COMMUNITY CHANGE (SUCCESSION)
Forest Successional Processes in the E. S. George Reserve, Livingston County, Michigan Ivette Perfecto John Vandermeer.
Impact of plot size on the effect of competition in individual-tree models and their applications Jari Hynynen & Risto Ojansuu Finnish Forest Research.
Deliverable 2.3 CVS will construct refined guidelines for using plot data and taxon distribution data to develop restoration targets for specific sites.
Null models and observed patterns of native and exotic diversity: Does native richness repel invasion? Rebecca L. Brown, 1,2 Jason D. Fridley, 1 and John.
Structure and Demography of Tree Communities in Tropical Secondary Forest Recovering From Logging Keala Cummings and Dr. Diane Thomson 2007 Keala Cummings.
COMMUNITY CHANGE (SUCCESSION) Krebs cpt. 21; pages ; 431.
Decline of Eastern Hemlock due to Hemlock Woolly Adelgid
Effect of silvicultural and prescribed fire treatments on coarse woody debris dynamics in a sierran old growth mixed-conifer forest. Jim Innes and Malcolm.
Fine-scale species-area relationships of the vascular flora of the Southeast (USA) Jason Fridley, Robert Peet, Peter White, Joel Gramling, Todd Jobe, Jessica.
Advantages of Monitoring Vegetation Restoration With the Carolina Vegetation Survey Protocol M. Forbes Boyle, Robert K. Peet, Thomas R. Wentworth, and.
Community Ecology. Climate and the Distribution of Ecological Communities n Communities are assemblages of large numbers of species that all interact.
What Species (Engelmann Spruce or Subalpine Fir) Has the Most Important Value Based On the Aspect Of the Northern, Southern, Western, and Eastern slope.
Temperate Forests. Temperate forests are found primarily in North America and Eurasia.
Effects of Silvicultural Practices on Woody Vegetation John Kabrick, Steve Shifley, and Dan Dey – USDA Forest Service Northern Research Station Randy Jensen,
Opportunities for Restoring Second Growth Ecosystems in Staney Creek: Scientific Principles.
Tree distribution patterns in the southwest Jemez Mountains Kamal Humagain 1, Robert Cox 1, and James Cain 2 1 Texas Tech University 2 New Mexico State.
A plant or animal species small in numbers and is in endanger of becoming extinct. The most common reasons for endangerment are as follows: overhunting,
VIRTUAL ECOLOGICAL INQUIRY MODULE: A Collaborative Project Between TAMU-ITS Center and CAS-CNIC Presented by: X. Ben Wu and Stephanie L. Knight Department.
FLORA AND VEGETATION OF THE KOKIWANEE NATURE PRESERVE David J. Hicks and Teresa M. Michaelis Biology Department, Manchester College North Manchester, IN.
The effects of selective harvesting on upland oak/hickory forests David Dyson and Jessi Ouzts Independent Study Project, Advent 2005 Introduction Coarse.
Using dendroecological techniques to interpret the response of trees to environmental change at the Vermont Monitoring Cooperative’s Mount Mansfield study.
How do forest ecosystems respond to environmental change?
Forest Survey Can you identify this tree?. Red Maple.
Alex Robertson Vegetation Ecology Intro From a study on windows of opportunity for Vaccinium species, Eriksson and Fröborg (1996) found that decaying.
Hemiparasitism: a way station to holoparasitism or an evolutionary stable strategy? Prof. Joseph E. Armstrong Illinois State University Behavior, Evolution,
2013 2nd Quizzes Provide three traits that are characteristic of the fungi What are the three major groups of fungi we discussed in class Please differentiate.
Suborna Shekhor Ahmed Department of Forest Resources Management Faculty of Forestry, UBC Western Mensurationists Conference Missoula, MT June 20 to 22,
Vermont’s Future Forests Sandy Wilmot Forests, Parks & Recreation.
Integrating field data and remote sensing to study secondary forests in Amazonian rural settlements Mateus Batistella Embrapa Satellite.
Julia Roberts and Dr. David Vandermast Elon University.
How do plant communities change over time?
Thinning mixed-species stands of Douglas-fir and western hemlock in the presence of Swiss needle cast Junhui Zhao, Douglas A. Maguire, Douglas B. Mainwaring,
Compositional Shifts in Undisturbed Neotropical Forests: Effects of Climate Change? William F. Laurance 1,2 & Richard Condit 1 William F. Laurance 1,2.
Population Parameters – Chapter 9. Population – a group of organisms of the same species occupying a particular space at a particular time. Demes – groups.
A Winter Comparison Study of Dominant Alpine Plant Communities in the Southern Rocky Mountains and the Chugach Mountains of Southern Alaska What factors.
Modeling Hemlock (Tsuga canadensis) Health During an Infestation of Hemlock Wooly Adelgid (Adelges tsguae) Christy Rollinson ‘08 Rufus Nicoll ‘09.
Multi-institutional collaborative program. Established in 1988 to document the composition and status of natural vegetation of the Carolinas. Provides.
Over 80 years Late-successional Old-growth Raymond Davis Monitoring Lead Older Forests and Spotted Owls (Northwest Forest Plan Area) Defining Older Forests.
Healthy Forests, Healthy Deer Collaborative Deer Management Outreach Initiative.
Steven Katovich USDA Forest Service Exotic and Invasive Insects and Pathogens new and expanding threats.
Improving fine root sampling methods for landscape-level ecosystem studies using root anatomy and morphology Kirsten Lloyd M.S. Candidate Complex Systems.
More Ecosystems Red Spruce – Fraser Fir Forest in the Appalachian Mountains of North Carolina Grassland on rolling hills in North Dakota Mid-montane conifer.
A Study of Factors Affecting Biological Diversity Based On The Auburn Forest and Nokomis Forest Auburn Nokomis Collin Li, Eric Tom, Benjamin Park, Cindy.
Chapter 10 Ecological Restoration. The Balance of Nature –An environmental myth that states that the natural environment, when not influenced by human.
Vegetation Census Lab. Field Trip to Sessions Woods.
Impact of mining activity on Lake Duparquet shoreline forest dynamics Hugo Asselin (Québec) John Brown (Missouri) Mary Harner (New Mexico) Christina Longbrake.
Glenn Kohler FS 533 Background photo: eastern hemlock mortality, Bill Ciesla Silvicultural treatments for management of the hemlock woolly adelgid in the.
Kendra G. Schotzko & Stephen P. Cook 19 September 2014 University of Idaho Moscow, Idaho Mountain Pine Beetle Impacts on Whitebark Pine: Mortality and.
Annualized diameter and height growth equations for plantation grown Douglas- fir, western hemlock, and red alder Aaron Weiskittel 1, Sean Garber 1, Greg.
Community Ecology Patterns in Communities Chapter 20 Section 2 Pages
Feeding Across the ESN: Studying Herbivore-Ecosystem Interactions Following Fire in Black Spruce Forests Characterizing and inferring patterns and processes.
Ecology 8310 Population (and Community) Ecology Communities in Space (Metacommunities) Island Biogeography (an early view) Evolving views Similarity in.
A Comparison of Seed Longevity of Eastern Tree Species Jillian Pieciak and Dr. Vandermast Elon University, Elon, NC Aged seeds will have lower overall.
F OREST P EST O UTREACH S URVEY P ROJECT Early Detector Training.
Vegetation Profile as applied in Interior Alaska
Hemiptera: Adelgidae tsugae Annad
Jing Hu University of Queensland
Presentation transcript:

Community dynamics in old growth and second growth hemlock forests

Questions What impact, if any, is the hemlock woolly adelgid having on eastern hemlocks in North Carolina? Are other tree species responding with respect to relative density, relative basal area or importance value? How does species richness increase with area in eastern hemlock forests? How does the species area relationship change over time in eastern hemlock forests?

Great Smoky Mountains National Park Joyce Kilmer Memorial Forest Highlands Ranger District Plots 11 Second growth Ave. Elev: 2617 ft 12 Old growth Ave. Elev: 3045 ft Second growth Old growth Field sites of second growth and old growth hemlock communities in western North Carolina

Carolina Vegetation Survey protocol 50 m 20 m 10 total modules for trees 4 intensively sampled modules for herbs

10 cm 30 cm 1 m 3.3 m 10 m Intensively Sampled Module

Questions What impact, if any, is the hemlock woolly adelgid having on eastern hemlocks in North Carolina? Are other tree species responding with respect to relative density, relative basal area or importance value? How does species richness increase with area in eastern hemlock forests? How does the species area relationship change over time in eastern hemlock forests?

Life history of the hemlock woolly adelgid The hemlock woolly adelgid has two hosts: –Tsuga sp. Passive dispersal Asexual reproduction Density dependent shift to a winged sexuperae –Picea sp. Winged sexuperae Sexual reproduction No native spruce are suitable hosts This results in two waves of mortality in hemlock with the smaller hemlocks dying first.

Tsuga can Acer rub Betula len Rhodo max Kalmia lat Average change in abundance of small (0 – 2.5 cm dbh) individuals Old Growth Second Growth ** Average change in abundance

Questions What impact, if any, is the hemlock woolly adelgid having on eastern hemlocks in North Carolina? Are other tree species responding with respect to relative density, relative basal area or importance value? How does species richness increase with area in eastern hemlock forests? How does the species area relationship change over time in eastern hemlock forests?

Relative Value Relative density, relative basal area and importance value in old growth forests Tsuga canadensis Acer rubrum Betula lenta Rhododendron maximum Kalmia latifolia *

Relative density, relative basal area and importance value in second growth forests Relative Value Tsuga canadensis Acer rubrum Betula lenta Rhododendron maximum Kalmia latifolia * *

Summary of successional change in tree layer Small hemlocks are decreasing in absolute abundance in both old growth and second growth forests, with no corresponding increase in larger size classes. In old growth forests, Rhododendron maximum is increasing in relative abundance. In secondary growth forests, Tsuga canadensis is increasing in relative abundance and importance values.

Questions What impact, if any, is the hemlock woolly adelgid having on eastern hemlocks in North Carolina? Are other tree species responding with respect to relative density, relative basal area or importance value? How does species richness increase with area in eastern hemlock forests? How does the species area relationship change over time in eastern hemlock forests?

Carolina Vegetation Survey protocol 50 m 20 m 10 total modules for trees 4 intensively sampled modules for herbs

Species richness at 1000 m 2 StageMeanRange Post-adelgid, old growth Pre-adelgid, old growth Post-adelgid, second growth Pre-adelgid, second growth

Average species richness in old growth hemlock forests at increasing scales (m 2 ) Pre-adelgidPost-adelgid

Average species richness in second growth hemlock forests at increasing scales (m 2 ) Pre-adelgidPost-adelgid

Old GrowthSecond Growth Average change in species richness at increasing scales in old growth and second growth hemlock forests 0 ** Average change in species richness

Questions What impact, if any, is the hemlock woolly adelgid having on eastern hemlocks in North Carolina? Are other tree species responding with respect to relative density, relative basal area or importance value? How does species richness increase with area in eastern hemlock forests? How does the species area relationship change over time in eastern hemlock forests?

Pre-adelgid, old growth Log 10 area Species-area relationships in hemlock forests before the hemlock woolly adelgid Log 10 species richness

Log 10 area Pre-adelgid, second growth Species-area relationships in hemlock forests before the hemlock woolly adelgid Log 10 species richness

Pre-adelgid, old growth Pre-adelgid, second growth Log 10 area Species-area relationships in hemlock forests before the hemlock woolly adelgid Log 10 species richness

Log 10 area Pre-adelgid, old growth Pre-adelgid, second growth Species-area relationships in hemlock forests before the hemlock woolly adelgid Log 10 species richness

Log 10 area Log 10 species richness Post-adelgid, old growth Post-adelgid, second growth Species-area relationships in hemlock forests after the hemlock woolly adelgid

Log 10 species richness Log 10 area Post-adelgid, old growth Post-adelgid, second growth

Post-adelgid, old growth Pre-adelgid, old growth Log 10 species richness Log 10 area Change in the species area relationship over time in old growth forests

Post-adelgid, second growth Pre-adelgid, second growth Log 10 species richness Log 10 area Change in the species area relationship over time in second growth forests

Post-adelgid, old growth Pre-adelgid, old growth Post-adelgid, second growth Pre-adelgid, second growth Log 10 species richness Log 10 area Change in the species area relationship over time

Parameters of species area relationship Log S = Z Log A + Log C StageZ valueSE Post-adelgid, old-growth forest Pre-adelgid, old-growth forest Post-adelgid, second-growth forest Pre-adelgid, second-growth forest

Summary of species richness and species area relationship results Species richness decreased slightly at the largest scales in second growth forests. The primary difference in species area relationships are between second growth and old growth. There is no difference in species area relationships from before and after the hemlock woolly adelgid. –Time may not be long enough. In old growth forests, species do not accumulate with area as quickly as in second growth forests.

Acknowledgments Committee –Robert Wyatt –Bob Peet –Peter White –Tom Wentworth –Allan Strand US Forest Service National Park Service Highlands Biological Station Plant Ecology Lab at UNC Karen Patterson, Claire Newell, Dan Pittillo,Larissa Knebel, Aaron Cooper