Investigating the mechanisms by which available nitrogen affects biodiversity of a plant community native to the Indiana Dunes National Lakeshore Eric.

Slides:



Advertisements
Similar presentations
Plant Attributes ‘Leggy’ Plants Foxglove (Penstemon) White Sage
Advertisements

Module #6 Forage Selection Pine Silvopasture in the Southeast.
WRAP Meeting Nov 11, 2009 Ozone and Nitrogen Concerns in Western National Parks Chris Shaver Air Resources Division National Park Service.
Prairie Restoration: Increasing Warm-Season Native Grasses with Fire, Herbicide, and Nitrogen Application Shauna Waughtel, S.A. Clay, A. Smart, D.E. Clay,
Soil Organic Carbon and Nitrogen Accumulation of Rhizoma Perennial Peanut and Bahiagrass Grown under Elevated CO 2 and Temperature Leon H. Allen, ARS-FL.
Restoration Techniques, & Commonly Found Prairie Plants Lake Katherine Nature Center & Botanic Garden.
Effect of atmospheric deposition of nitrogen on the fixation and assimilation of nitrogen by wild lupine (Lupinus perennis) in the sand dunes of Lake Michigan.
Grasses, Grass-likes & Forbs Cumulative FLASH CARDS Plants to be learned before the field trip. In Random Order.
Multiple Native Species Planting Mixtures “It’s Time for a Change!!!” GRASSLANDER Chuck Grimes Rt 1 Box 56 Hennessey OK 73742
INTRODUCTION Figure 1: Seedling germination success by planting technique plus rainfall amount and date at the Poolesville location during fall BC.
Illinois Plant Communities – Prairie Ecosystems.
Michelle Trogdon GEOG 4401/5401 Soils Geography Fall 2007 – Univ of Colorado, Boulder.
Illinois Plant Communities – Prairie Ecosystems.
The effects of a spring burn on noxious weeds in a tallgrass prairie E. Vander Broek, T. Tracy, J. Boersma, and R. Weeks Biology Department, Northwestern.
Soil-mediated effects of a CO 2 gradient on grassland productivity: Interactions with resources and species change. Philip A. Fay USDA-ARS Grassland, Soil,
Impacts of Waterfowl and Water Levels on Wetland Vegetation Jay Frentress, Adrienne Froelich, David Lodge, Department of Biological Sciences, University.
An observation: “Tens Rule” From Williamson & Fitter (1996) Ecology 77: Only ~10% of imported species escape to wild Only ~10% of species that.
Landscapes in Indiana Dunes Landscape features are dynamic and can be dated: 100s – 1000s of years for dunes 10s – 100s of years for blowouts Big blowout.
The Value of Native Ecosystems
EFFECT OF HARVEST REMOVAL ON PRODUCTIVITY OF A 15-YEAR-OLD DOUGLAS-FIR PLANTATION. by Dale W. Cole and Jana E. Compton University of Washington and Harvard.
The Effects of Nitrogen Fertilization on Nutrient Cycling and Forest Productivity By: Eric Sucre.
Growing Native Plants in Chisago County Tom Dickhudt March 1, 2005.
First Set of Grasses – FLASH CARDS
Grasses & Grass-likes Cumulative – FLASH CARDS Plants to be learned before the field trip. In Random Order.
Does Biological Diversity Control Ecosystem Function?
Eighteen Years of Acid Wet Deposition at Mt. Mansfield Goals & Objectives One goal of the VMC is to understand the sources, mechanisms, and effects of.
INTERACTIONS BETWEEN PERIPHYTON AND MACROPHYTES IN THE SOUTHERN EVERGLADES MARL PRAIRIES, FLORIDA, USA Anna Wachnicka 1, Evelyn Gaiser 1,2, David Jones.
The Alternative World of Biofuels Hailey DeVries IB Major.
Affects of Density on Intraspecific Competition in Marigolds Eric Flatt Undergraduate Student (Marine Biology Concentration) Department of Biology Tennessee.
Effects of Intraspecific Competition on Varying Groups of Marigolds Tiffany Landis Microbiology Major Tennessee Technological University Cookeville, TN.
Dormancy breaking and germination techniques for Dichanthelium leibergii, a cool season prairie grass Acknowledgments Thanks to Stuart Wagenius for help.
PROJECT SUMMARY Low-input high-diversity (LIHD) grasslands are a promising system for biofuel production as they provide additional environmental benefits.
Regeneration of Natural Pasture in Enclosures for Parthenium Weed Management in the Rangeland of Jigjiga, Somali Regional State, Ethiopia B Y Lisanework.
Introduction: Globally, atmospheric concentrations of CO 2 are rising, and are expected to increase forest productivity and carbon storage. However, forest.
How Plants Grow & Respond to Disturbance. Succession & Disturbance  Community change is driven by successional forces: Immigration and establishment.
How Plants Grow & Respond to Disturbance. Succession & Disturbance  Community change is driven by successional forces: Immigration and establishment.
Non-destructive Estimation of Net Primary Production in Urban Rain Gardens Design Plastic pots (open cylinders, diameter 36 cm and height 92 cm) were filled.
Ecological Succession.  Ecological succession is the observed process of change in the species structure of an ecological community over time.
Abstract We conducted a field experiment where diversity was indirectly manipulated by altering the number of initially planted species (6-30 species).
The Coefficient of Germination Velocity (CGV) is a measure of the number of seeds germinating in a period of time. Generally, the CGV increases as more.
Global Change and Southern California Ecosystems Rebecca Aicher UCI GK-12 March 7, 2009.
The Nature Conservancy: A Pilot Season for Cooperative Grassland Monitoring Meredith Cornett Director of Conservation Science The Nature Conservancy Minnesota,
What are edaphic effects? Edaphic effects are soil characteristics that modify growth and development of plant species: –Organic matter –Inorganic minerals.
Diversity Productivity Relationships Species Richness Seminar October 21, 2003.
Energy allocation: Studies on Goldenrods Abrahamson and Gadgil (1973) studied goldenrods along what they described as a 'disturbance gradient'. Species.
 Grassland biomes: large, rolling terrains of grasses, flowers and herbs  Latitude, soil and local climates: determine what kinds of plants grow  Region:
Chapter 1 Part 3 Populations.  Understand how limiting factors affect populations  Explain how limiting factors are related to carrying capacity  Identify.
Wild About Radishes 8 th Grade Inquiry Science Benchmark Assessment.
Ecological Risk Assessment of Switchgrass (Panicum virgatum) in Connecticut A review of published floras and approximately 2000 herbarium specimens at.
Introduction The structure of plant communities is believed to be governed in part by competition. Allelopathy is a well- documented competitive interaction.
Michael H. Graf, Undergraduate Student
Figure 9. Under conditions of higher soil nitrogen availability, grasses (or other non-legumes) may dominate the cover crop stand. Black indicates nitrogen.
CARBON LIFE CYCLE ANALYSIS OF BIOENERGY CROPS PLANTED IN THE MARGINAL SITES IN LOWER MISSISSIPPI ALLUVIAL VALLEY K.C. Dipesh1, Michael.
Relative importance of genotypic richness vs. phenotypic plasticity
Increasing Diversity of Native Biofuel Plantings Using Simple Mixtures
Early-flowering forbs
Great Plains – Flash Card Wildland Plants Identification
Hardcore Ethan, Cory, Richard, and Joe Green 11/3/11
Management and Life Cycle Assessment of Bioenergy Crop Production
Wildflower Trails of Mississippi
Which affect the rate of photosynthesis
The Scientific Method.
The Scientific Method.
Lesson Seventeen: Grass Seedings.
Drawing Conclusions.
Great Plains – Flash Card Wildland Plants Identification
First Set of Grasses – FLASH CARDS
Forage Selection Pine Silvopasture in the Southeast 4/5/
GERMINATION Seed experiment.
Presentation transcript:

Investigating the mechanisms by which available nitrogen affects biodiversity of a plant community native to the Indiana Dunes National Lakeshore Eric Bird Purdue University Calumet Flora Richardson Fellowship Recipient

Concern Atmospheric deposition of nitrogen is high in the Midwestern and Eastern United States The Indiana Dunes receive approximately 15kg ha -1 y -1 nitrogen as wet deposition Research has shown that increases in available nitrogen to low nitrogen ecosystems affects species composition and can have an overall negative affect on biodiversity

Preliminary research shows that ammonium nitrate treatment Reduces the total biomass of some species Alters how species allocate biomass (aboveground vs. belowground) Reduces the germination success of some species

Setup Use laboratory experiments to determine which species are hindered by nitrogen treatment and… Use this information to predict which species will occur less frequently in a constructed native plant community grown in the field against a gradient of available nitrogen

Species investigated Schizachyrium scoparium – little bluestem grass Elymus canadensis – Canada wild rye Panicum virgatum – switchgrass Sorghastrum nutans – Indiangrass Rudbeckia hirta – black eyed susan Echinacea purpurea – purple cone flower Dalea purpurea – purple prairie clover Monarda punctata – dotted mint Liatris aspera – rough blazing star Lupinus perennis - lupine

Experiments Biomass allocation – greenhouse Germination – laboratory Aboveground biomass production – field Biodiversity – field Competition – field

Biomass allocation greenhouse Purpose: to determine the relationship between available nitrogen and biomass allocation of ten native species

Biomass allocation greenhouse Hypothesis: if amount of ammonium nitrate increases then some species will allocate more biomass to aboveground growth while others will not.

Biomass allocation greenhouse Four treatment groups (n = 5): – control – 30kg ha -1 – 60kg ha -1 – 120kg ha -1 Biomass will be harvested after approximately 6 months of growth.

Biomass allocation greenhouse Prediction 1: species that allocate more biomass to aboveground growth will outcompete other species in the field as available nitrogen increases

Competition and biomass allocation field Purpose: to determine whether aboveground or belowground biomass allocation increases the relative dominance of a species in a high nitrogen environment

Preliminary research biomass allocation Table 1 aboveground and belowground percent biomass for E. canadensis and S. scoparium (n = 5) Biomass PercentageSchizachyrium scopariumElymus canadensis Control Mean (g) Nitrogen Mean (g)p-value Control Mean (g) Nitrogen Mean (g)p-value Aboveground50.3 ± ± ± ± Belowground49.7 ± ± ± ±

Competition and biomass allocation field Prediction 1: species that allocate more biomass to aboveground growth will outcompete other species in the field as available nitrogen increases Hypothesis 1: if biomass allocation determines relative dominance then one of the two species should dominate at increased nitrogen levels Hypothesis 2: if preliminary data and prediction 1 are correct then in high treatment groups S. scoparium will allocate more biomass to aboveground growth and will increase in relative dominance over E. canadensis

Competition and biomass allocation field Two species: E. canadensis, and S. scoparium Four treatment groups (n = 5): – Control – 30kg ha -1 – 60kg ha -1 – 120kg ha -1 Rectangular plastic containers are buried at the field site and half seeded with each of the two species. After one growing season the percent coverage by each species is determined

Germination laboratory Purpose: to determine the relationship between the concentration of ammonium nitrate and the germination success of ten native species. Hypothesis: if ammonium nitrate concentration is increased then the germination success of most species will be reduced

Preliminary research germination

Germination laboratory Four treatments (n = 7): – Control – 1000ppm – 2000ppm – 4000ppm Seeds germinated in petri dishes containing mineral sand at 22°C for 6 weeks Number of germinated seeds recorded each week

Germination laboratory Prediction 2: Species that are most successful at germinating at higher end of the spectrum should occur more frequently in the field as ammonium nitrate levels increase

Biodiversity field Purpose: to determine whether available nitrogen affects biodiversity of a plant community native to the Indiana dunes

Biodiversity field Prediction 1: species that allocate more biomass to aboveground growth will outcompete other species in the field as available nitrogen increases Prediction 2: Species that are most successful at germinating at higher end of the spectrum should occur more frequently in the field as ammonium nitrate levels increase

Biodiversity field Hypothesis 1: if nitrogen levels increase then biodiversity will decrease Hypothesis 2: if biodiversity decreases as a result of nitrogen additions then predictions 1 and 2 will be true

Biodiversity field Four treatment groups (n = 5): – Control – 30kg ha -1 – 60kg ha -1 – 120kg ha -1 Species are seeded in 2x2m plots at field site. Percent coverage and aboveground biomass of each species is determined after two seasons.

Summary It is expected that nitrogen additions will – Reduce germination of most species – Cause some species to allocate more biomass aboveground Therefore – As nitrogen levels increase few species with high germination success and aboveground biomass allocation will begin to dominate and biodiversity will decline as a result