Methods Tree selection varied slightly at the four different locations. On the rim and river trails, I walked along established paths and selected the.

Slides:



Advertisements
Similar presentations
Diversity of Surface Active Invertebrate Communities at the DePauw Nature Park and Arboretum Aaron Randolph, Department of Biology, DePauw University,
Advertisements

 Sycamore Tree Health, Dispersal, and Soil Composition in Quarry Bottom Flood Zones Zachary R. Young, Sarah Minor, Hunter Schouweiler.
Patterns and processes of recovery in and around an Indiana limestone quarry Vanessa L. Artman, Dana A. Dudle Bryan Helm, David Pope, and Aaron Randolph.
Investigating the relationship between species richness and wilderness in the coastal temperate rainforest of Southeast Alaska. This poster represents.
Movement Patterns and Microhabitat of Red-Backed Salamanders (Plethodon cinereus) Introduction Studying movements and microhabitat of a common, widespread.
Height to DBH Ratio in N. Olympic Forests Karsten Turrey, North Olympic Peninsula Skills Center Natural Resources Prior Knowledge I know that as trees.
History of Succession. Succession Changes that forests undergo are part of a process.
Ecological Composition and Relative Health of the Forested Sites at the DePauw Nature Park and Proposed Management Strategies Figure 6. Composition and.
Big Walnut Creek Forest A study of soil and tree species Brett Bohlander Brittany Mohrman Tory Pavlovich.
Brief History of Site Quality Estimation from a Forest Mensuration Perspective Eric C. Turnblom ESRM Forest Soils and Site Productivity - Autumn.
Lodgepole Pine / Ponderosa Pine Ecotone By Tyler Bieneman Lodgepole Pine / Limber Pine Ecotone VS. Winter Ecology – Spring 2005 Mountain Research Station.
o What were we looking at? o The Pit Crew studied soil patterns throughout the landscape.
Fall River Long-term Productivity Study : Predictions of Pre-harvest Biomass and Nutrient Pools K. Petersen, B. Strahm, C. Licata, B. Flaming, E. Sucre,
Figure 1. Age distribution of white pines in January 2006, in Range Pond State Park near Plains Road. Mean age was 49 ± 5.8 yr. N = 44 trees. Age based.
FACTORS AFFECTING NESTING SUCCESS OF COEXISTING SHOREBIRDS AT GREAT SALT LAKE, UTAH John F. Cavitt, Department of Zoology, Weber State University The Great.
Comparative Growth of the Spiked Fescue on a Northwest and a Southwest Facing Slope By Sam Humphrey July 18, 2013 Vegetation Ecology CU Mountain Research.
Introduction Subalpine meadows play a crucial role in species diversity, supporting many endangered species of plant and wildlife. Subalpine meadows play.
+ Trail Disturbance in the Alpine Meadow on Arapaho Pass and Mount Yale Marieta Bialek Vegetation Ecology 2013 Mountain Research Station University of.
Receding water levels in Ogallala aquifer are threatening the sustainability of irrigated agriculture in the High Plains of Eastern New Mexico and West.
Precipitation Effects on Tree Ring Width for Ulmus americana L
Biomes FIELD BIOLOGY & METHODOLOGY Fall 2014 Althoff Lecture 04.
Foliage and Branch Biomass Prediction an allometric approach.
Effect of a Tropical Storm in a Urban Secondary Forest in Humacao, Puerto Rico Cintrón Sol Taína 1,, Carmen Zayas 1, Natalia Piñeiro 1, Joel Soto 2 y Denny.
The effects of Intraspecific competition in Trifolium repens L. Brian Roberts Student Education Department Tennessee Tech University Cookeville, Tennessee.
Effect of Fire on Soil ability to Sustain Plant Life Becca Gentile and Erica Garroutte.
Kim Tarde Vegetation Ecology Summer 2014 Mountain Research Station, University of Colorado, Boulder.
Scientific Inquiry & Skills
A Statistical Analysis of Seedlings Planted in the Encampment Forest Association By: Tony Nixon.
Composition of the Songbird Community at the DePauw Nature Park and Arboretum Libby Allard, V. Artman, K. Reed, K. Koehler, Department of Biology, DePauw.
Yellowstone National Park, Succession is the gradual change in a community involving species in one stage being replaced by different species in.
Dendroecology of Piñon Trees At the Los Pinos Mountains on the Sevilleta National Wildlife Refuge By Jason Lopez.
Option G: Ecology and Conservation Chpt. 18: pages
WP2. Adaptability and Productivity Field Trials Results from the fourth growing period and comparison of the results recorded from the years 2003, 2004.
UNIT 5 Ecosystems ABIOTIC FACTORS AFFECT THE BIOCENOSIS Natural Science 2. Secondary Education.
Effect of retained trees on growth and structure of young Scots pine stands Juha Ruuska, Sauli Valkonen and Jouni Siipilehto Finnish Forest Research Institute,
Welcome! §Please read the board completely. §Please get out your Ecology objectives #1- 5 and review with your neighbor for the quiz. (add review ideas.
Approach: Samples were obtained from 4 different plots of land, each with a different land-use. The land uses that were examined were a grassland (hayed),
Effects of Regeneration Abundance on Predicted Development of Interior Douglas-fir Stands By Cornel Lencar Graduate Student, Faculty of Forestry University.
Results of Long-Term Experiments With Conservation Tillage in Austria Introduction On-site and off-site damages of soil erosion cause serious problems.
Ecological Succession Objectives 1.Explain what succession is 2.Explain the process of ecological succession 3.Explain the role that plants play in maintaining.
PCB 3043L - General Ecology Data Analysis. OUTLINE Organizing an ecological study Basic sampling terminology Statistical analysis of data –Why use statistics?
The effects of the 2002 Hayman Fire on the ponderosa pine/bunch grass ecosystem Nick Kelley Blake Schnebly
Birds on the Edge Forest edge effects on bird assemblage size and composition in the Chuckanut Mountains Drew Schwitters Department of Environmental Sciences,
 Comparing Vegetation in a Riparian Zone to an Upland Area in a Colorado Montane Forest By: Abby Branson Vegetation Ecology, Summer 2013 Mountain Research.
FORESTRY TEST BASICS. How To Measure the Diameter of a Tree? Stand next to the trunk (if on an non-level slope – then stand on the uphill side of the.
Forest floor invasion results, 2002 Questions we asked: 1. Last year we found woody stem density was 65% lower in Vinca areas than on the natural forest.
PCB 3043L - General Ecology Data Analysis. PCB 3043L - General Ecology Data Analysis.
Forest Dynamics on the Hickory Ridge of St. Catherines Island Alastair Keith-Lucas Forestry and Geology Department, University of the South Introduction.
Climate Change in the Mind of a College Student A Cross-Sectional Study on Climate Change Perceptions at the University of Oklahoma Benjamin Ignac, Aparna.
PCB 3043L - General Ecology Data Analysis.
mQ OBJECTIVES The student should be able to: 1.list and describe the steps of the scientific method 2.define.
Stand Development. Site Capability The ability of a forest to grow is related directly to physical site factors. Favourable physical factors create better.
The Effect of Fuel Treatments on the Invasion of Nonnative Plants Kyle E. Merriam 1, Jon E. Keeley 1, and Jan L. Beyers 2. [1] USGS Western Ecological.
Energy allocation: Studies on Goldenrods Abrahamson and Gadgil (1973) studied goldenrods along what they described as a 'disturbance gradient'. Species.
Our data suggests that the Habitat Diversity Theory better explains species richness of woody plants on islands in the BWCAW than the Equilibrium Theory.
Materials: LI-COR LAI-2200 Plant Canopy Analyzer FV2200 software Excel Rstudio Methods and Study Site: LAI measurements using an indirect, optical method.
Comparison of Odonata Populations in Natural and Constructed Emergent Wetlands in the Bluegrass Region of Kentucky Introduction Wetlands provide valuable.
Effects of Prairie Management on Soil Characteristics and Bees METHODS RESULTS  Soil Characteristics Analysis of variance (ANOVA) suggests that there.
PCB 3043L - General Ecology Data Analysis Organizing an ecological study What is the aim of the study? What is the main question being asked? What are.
Fir Douglas or cedar red western?
PCB 3043L - General Ecology Data Analysis.
Species Diversity Comparison North and South Slopes
Additional Data Collection in 2017
5-3 How Do Communities and Ecosystems Respond to Changing Environmental Conditions? Concept 5-3 The structure and species composition of communities and.
A Comparison of Riparian Vegetation Structures
Vegetation Dynamics of the NE and NW slopes of Betasso Preserve
National Forest Inventory for Great Britain
Unit 6: Comparing Two Populations or Groups
Tina Nguyen Vegetation Ecology Summer 2018
The effects of Canopy Cover on Herbaceous Vegetation
Presentation transcript:

Methods Tree selection varied slightly at the four different locations. On the rim and river trails, I walked along established paths and selected the first 50 trees within 3 meters of the path. In the Meadow, I selected all the trees in the grassy meadow section of the plot and a random subset of trees surrounding the meadow to obtain 100 sample trees. In the quarry bottom, I walked along 5 established transects and selected all trees within 2 meters of the line. This method yielded around 275 trees in the quarry bottom. Growth of each tree was measured in three ways. I first took the diameter at breast height (DBH) using a meter tape or ruler. I then determined the height of the tree and the height of its lowest live branch using a meter tape or clinometer (Fig. 5). The age was estimated for a subset of 39 trees. The trees from each location were divided into four size groups from which three trees were selected. The size groups, which were based on DBH, were: 8 cm. The trees were aged by counting the rings on tree cores (Fig. 6) or discs (Fig. 7). Conclusions & Future Work We have discovered some interesting growing patterns for sycamores at the quarry and other sites. We know that the quarry and rim trail sycamores have similar growth patterns, in much the same way the trees at the river trail and meadow grow at similar rates. We know that location has significant effects on total height, DBH, and height of lowest live limbs of the sycamores. Now that we know what is going on, here are some ideas for future research: 1. Study competition intensity at the four locations 2. Study water availability in the soil at the different locations 3. Study history of disturbance and land use at the sites—Were the sycamore trees planted in the quarry? 4. More detailed spatial analysis of sycamores and their growing areas 5. Continue monitoring sycamores over long-term because this is a great opportunity to observe succession in action!! Introduction The Depauw Nature Park includes a variety of habitats suitable for plant life, such as riversides, early-successional meadows, forests, and an abandoned limestone quarry. These habitats vary substantially in vegetative composition, soil moisture, and competitive environment. The quarry bottom (Fig.1) is an example of a recently disturbed primary successional area where conditions are very stressful but competition is minimal. The meadow (Fig. 2) exemplifies a secondary successional area where the soil has also been recently disturbed, and where plant density is high. The rim trail (Fig. 3), which encircles the quarry bottom and borders forested land, is dry, rocky, and more stressful (in terms of water availability) than the river trail. The river trail is a floodplain (Fig. 4), home to alluvial soils. It has experienced less recent disturbance than the other sites. The one thing these four areas have in common is the sycamore tree(Platanus occidentalis.) Needing only moisture, sunlight, and small amounts of soil, the sycamores can survive in a variety of habitats and a wide range of soils (USDA). With heights reaching up to 37 meters and diameters up to 4 meters (USDA), sycamores can be among the largest trees in mature Eastern deciduous forests. However, minimal resource requirements also make the sycamore one of the most prominent primary successional species to inhabit once-mined or disturbed areas. From 1928 to 1975, sycamore was one of the 10 most popular trees to plant on surface-mined soils in Indiana. Volunteer sycamore saplings were also found in small numbers on an abandoned limestone quarry in Oklahoma (Sullivan 1994). Hypothesis and Predictions We know that sycamores can grow in a wide range of habitats, but the goal of our study is to determine the effects such habitats can have on patterns and rates of tree growth. We predict that trees growing in the quarry bottom will be smaller and have lower limbs than trees of the same age growing in more wooded areas with better soil. Works Cited Nelson, Guy American Sycamore. United States Department of Agriculture-- National Resources Conservation Service Plant Guide. Rosiere, R. E. et al Revegetation of tripoli quarries in the Ozark Highlands of Oklahoma. Landscape and Urban Planning. 17: Sullivan, Janet Platanus occidentalis. In: Fire Effects Information System, U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: [2004, July 14]. Results & Discussion Does tree size vary across the four locations? Yes. The DBH, height, and lowest live limb differ significantly across the four locations (DBH: F=23.0, df= 3,303, p<.001; height: F=57.3, df= 3, 471, p<.001; lowest live limb: F= 56.3, df= 3, 468, p<.001). Trees at the rim and river trails consistently have a larger DBH, taller heights, and higher lowest live limb height than trees at the quarry or in the meadow (Fig. 8a-c). These data all make sense when taking into account the history and conditions of the four locations. Because the rim and river trails have had more time since their last disturbance, the trees are older and have larger DBH’s and heights than the younger trees at the quarry and meadow (Fig. 8a & b). There is also a difference in the average heights between the quarry and meadow. This can probably be explained by more intense competition for sunlight and less stressful abiotic conditions at the meadow than the quarry. Sycamores in the meadow have to compete with grasses, willows, and other plants for sunlight causing them to grow taller than sycamores at the quarry. The rim and river trail trees don’t have limbs growing as low to the ground as the limbs growing on the quarry and meadow trees (Fig. 8c), which may result from intense competition for sunlight and the shading out of lower limbs in the forested sites. The meadow, which has lowest live limbs much lower than the rim and river trails, has less competition for sunlight.. This permits lower live limb growth. The trees in the quarry encounter almost no competition for sunlight and have the lowest live limbs out of the four locations Does location affect the size distribution of trees? Yes. The size distributions vary significantly between location (Fig. 9; chi-square = 165.2, p<.001). These size distributions (based on DBH) reflect variation across the sites, in factors such as abiotic stress, competition, and human disturbance. The rim trail displays what could be considered an “expected” tree size distribution. The strong competition for sunlight and many years since the last disturbance seem to have encouraged growth and survival of larger trees. Younger trees in the population cannot compete for sunlight and nutrients, and have not thrived. The river trail has more small trees than expected. This may be due to a human-made opening on the trail where competition for sunlight is less intense, and many smaller trees have been able to survive. The remainder of the river trail has larger trees. The distribution of the trees in the meadow reflects the unique growing situation of that site. The majority of the smaller trees are located in the middle of the meadow, while the medium to large trees are generally located in areas surrounding the meadow where there has been less recent disturbance and more competition for sunlight. The quarry is arguably the most stressful environment at the nature park in terms of water and nutrient availability. It is somewhat surprising that the quarry supports as many large trees as it does. One possible explanation for this is the sycamores in the quarry are older on average than the meadow. This would explain the increased number of larger trees. Historical records may be used to test this hypothesis. Does location affect the heights and DBH’s of trees with respect to age? Yes. Overall, there is a significant positive relationship between age, DBH, and height. As trees age, they increase in height and DBH(Fig. 10). The slope of the relationship differs among the sites for age and height (F=3.045, df=3,34, p<.05) and age and DBH (F=3.217, df=3, 25, p<.05). The slopes and r 2 values show there is a trend towards trees growing taller and larger around for a given age at the river trail and meadow than at the quarry and rim trail. This would make sense if abiotic conditions were more stressful at the quarry and rim trail than the other sites. This trend supports the conclusion that the tree population at the meadow is younger than the other sites, including the quarry. With trees at the meadow growing tall more rapidly than trees at the quarry, and the trees being larger on average at the quarry, I would hypothesize that the meadow trees are younger and will eventually be larger than the quarry trees. Acknowledgements I would like to begin by thanking Aaron Randolph and Bryan Helm for all their help with the research throughout the summer. I would like to thank Professors Dana Dudle and Vanessa Artman for their guidance and patience. Last but not least, I would like to thank SRF and Depauw University for the opportunity and resources to do this research. Patterns of Sycamore (Platanus occidentalis) Growth at Four Locations Surrounding an Abandoned Limestone Quarry David Pope, B. Helm, A. Randolph, D. Dudle, V. Artman, Depauw University Figure 5. This diagram represents how the measurements were taken on each of the trees. Measurements were taken with a meter tape when possible, and a clinometer was used for the taller trees. Figure 7. This is one of the discs we used to age the smaller trees. Once sanded and coated with linseed oil, a dissecting scope was used to count the rings and age the trees. Figure 8. These are comparisons of the average heights (8a), average DBH’s (8b), and average lowest live limb heights (8c) at the four locations. Different letters indicate there is a significant statistical difference between the means. Figure 9. Tree size distribution at each of the four locations. The trees were placed into four size categories based on DBH and height. Figure 10. Growth rates of sycamores with respect to age. 10a compares age vs. height and 10b compares age vs. DBH at the four locations. 8a 8b 8c Figure 6. This tree core is how we aged the larger trees. This tree core was removed from the tree using an increment borer at 1.4 m above the ground. Once sanded and coated with polyurethane, we used a dissecting scope to count the growth rings on each core. Figure 1. Quarry Bottom (Primary Succession)Figure 2. Meadow (Secondary Succession) Figure 3. Rim TrailFigure 4. River Trail