Evaluating Phosphorus Limitation from the Maumee and Sandusky Rivers into Lake Erie Heather R. Kirkpatrick, Curtis C. Clevinger, Moumita M. Moitra, Darren.

Slides:



Advertisements
Similar presentations
Dynamics of cyanobacterial bloom formation Justin Chaffin Ph.D. F.T. Stone Laboratory Ohio Sea Grant The Ohio State University HABs.
Advertisements

E 5. Dissolved oxygen Outline biochemical oxygen demand (BOD) as a measure of oxygen- demanding wastes in water. Distinguish between aerobic and anaerobic.
F2- Microbes and the Environment Matt Oda Tia Rosehill Ross Tanaka.
Great Lakes Offshore Biological Desert and the Nearshore Slime Around the Tub David Rockwell Monitoring Indicators and Reporting Branch US EPA, Great Lakes.
University of Palestine Faculty of Engineering Environmental Sciences Course.
Ecosystem Ecology. Serengeti at Sunrise Biogeochemistry.
Summary of soil P levels and stratification GLPF Grant- Team meeting #5 July 23-24, 2013.
Effects of Conservation Tillage Systems on Dissolved Phosphorus Dr. David Baker Heidelberg University Tiffin, Ohio November 15, 2012 Davenport, IA.
Water Quality Tests.
Team Meeting #5, Great Lakes Protection Fund Grant A Phosphorus Soil Test Metric To Reduce Dissolved Phosphorus Loading to Lake Erie Heidelberg University.
Lake Erie Algal Source Tracking (LEAST) homas B. Bridgeman, University of Toledo Thomas B. Bridgeman, University of Toledo Cyndee L. Gruden University.
Great Lakes Observing System GLRI Tributary Monitoring Project
©2010 Elsevier, Inc. Chapter 18 Trophic State and Eutrophication Dodds & Whiles.
Harmful Algal Blooms in Western Lake Erie homas Bridgeman, University of Toledo Thomas Bridgeman, University of Toledo March 16, 2012.
Long-Term Volunteer Lake Monitoring in the Upper Woonasquatucket Watershed Linda Green URI Watershed Watch ,
Water Monitoring Lab. Why Test Water Quality? Water testing allows scientists and citizens to have a full understanding of what is affecting their stream.
Cycles of Matter Unlike the one-way flow of energy,
Water Quality Concerns in Ohio Waters What has been Happening in Lake Erie? Greg LaBarge, Field Specialist, Agronomic Systems.
Predicting HAB Strength (Western Basin) Pete Richards NCWQR-HU.
CONSEQUENCES OF RAW SEWAGE & NITRATE FERTILIZERS.
Garrett Stillings and Mark Martin Kentucky Division of Water Water Quality Branch Predicting Water Quality In Kentucky Lakes Using Remote Sensing.
An Investigation on the Effects of Climate Change On Algal Blooms in Lake Champlain Patricia Brousseau, Lauren Chicote, John Keyes, Jenna Mandelbaum, Christopher.
The Supplies The Product eutrophication: nutrient-driven stimulation of plant growth; contrast natural and cultural eutrophication; phosphorus is most.
Harmful Algal Blooms and Microcystin in the Tidal Fresh James River, Joe Wood, Ph.D. - Chesapeake Bay Foundation *Research performed while at VCU.
E 5. Dissolved oxygen Outline biochemical oxygen demand (BOD) as a measure of oxygen- demanding wastes in water. Distinguish between aerobic and anaerobic.
Pomme de Terre Lake Water Quality Summary Pomme de Terre Lake Water Quality Summary US Army Corps of Engineers Environmental Resources Section.
Eutrophication. Process of Eutrophication  natural process of the aging of a body of water  As more nutrients enter the water more organisms live and.
Water Monitoring. What/Why? Water testing Identifying water content Allows scientists to have a full understanding of what is affecting their stream or.
Learning outcomes Students should understand the following The environmental issues arising from the use of fertilisers. Leaching and eutrophication.
Water Quality.
Types of Water Pollution Sewage Disease-causing agents Sediment pollution Inorganic plant and algal nutrients Organic compounds Inorganic chemicals Thermal.
Water Use. What is the hydrologic cycle? The water cycle Precipitation Evaporation transpiration.
Symbiotic Relationships Mutualism: both species benefit from the relationship Commensalism: one organisms benefits and the other is neither helped nor.
Lake Erie Overview Dr. Jeffrey M. Reutter, Director Ohio Sea Grant and Stone Laboratory The Ohio State University Office of Congresswoman Marcy Kaptur.
Nitrogen in Lakes and Streams Wetzel Chapter 12 pp Joe Conroy 12 April 2004.
Fertilizers and the Environment
PH DO DIP TDP Bethany Remeniuk, Department of Biology, York College of Pennsylvania Is Microcystis aeruginosa an Initiator in a Positive Feedback Cycle.
The Gulf of Mexico Hypoxia Zone:. Mississippi River Basin.
Use of remote sensing in monitoring algal blooms in inland water bodies Anabel A. Lamaro Fortaleza 1-
Agricultural Pollutants and Fertilizers A farm is a high contributor to water pollution…why??? Rain typically washes nutrients and fertilizers off of.
Update on Lake Erie Nutrient and Algal Issues Gail Hesse Ohio Lake Erie Commission March 30, 2012.
5.4 Eutrophication.
Understanding and Monitoring Harmful Algal Blooms in Freshwaters Elena Litchman Michigan State University and Kellogg Biological Station.
Environmental Studies IDC3O3 Ms. Nguyen. * Amount of oxygen dissolved in water is a good indicator of water quality and the kinds of life it will support.
Biogeochemical Cycles CP Environmental Science. Biogeochemical Cycles The chemical interactions that exist between the atmosphere, hydrosphere, geosphere,
Dam Removal as a Solution to Increase Water Quality Matthew Nechvatal, Tim Granata Department of Civil and Environmental Engineering and Geodetic Science.
Nutrient Overload. DECOMPOSERS Nutrients Nitrogen Phosphorus Potassium Rabbit eats Plant and cycle Starts again Photosynthesis.
Role of Microorganisms in Ecosystems Microorganisms are organisms that are ___ __________ ___ _____ with the unaided eye. Microorganisms can either __________.
SCREENING FOR ALGAL TOXINS IN VOLUNTEER-MONITORED LAKES
LAKE ERIE SOURCE TRACKING OF HARMFUL ALGAL BLOOMS Douglas D. Kane 1, Joseph D. Conroy 2,3,
Variability of molecular assays Quality-control samples were collected and analyzed for cyanobacterial genes. Fourteen field concurrent replicates were.
Team Meeting #5, Great Lakes Protection Fund Grant A Phosphorus Soil Test Metric To Reduce Dissolved Phosphorus Loading to Lake Erie Heidelberg University.
Freshwater Harmful Algal Blooms (HABs) in California and SWAMP's Statewide Strategy California’s Surface Water Ambient Monitoring Program (SWAMP) Freshwater.
BeforeAfter Eutrophication. Eutrophication – nutrient enrichment of waters Major nutrients -phosphorus and nitrogen Consequences -increased plant growth.
EUTROPHICATION. IB Environmental Systems and Societies © by Lorne J. Young, published by TEACHINGpoint 2 Eutrophication is the natural process of the.
Environmental Chemistry Dissolved oxygen. Dissolved oxygen in water BOD = B iochemical O xygen D emand can be used as an indicator of the amount of organic.
Eutrophication. Paper Setup Eutrophication Not es : My Definit ion : Date ________ pg. ___ Video.
Aquatic Ecosystems as Sentinels of Change Field Station & Marine Lab Emerging Initiatives Workshop November 17, 2011 Colorado Springs, CO Craig Williamson.
Polluted Ponds – Blooming algae! Ponds can be fragile habitats where small amounts of pollution can have significant effects on the life in, on and around.
OR… The role of nutrients in the cultural eutrophication of Lake Erie Northwest Regional Office Office of the Great Lakes 18 April 2016.
Topic 4.4: Water Pollution
Hydrosphere Review Rapid Recall
Primary Productivity.
Lake Erie Fisheries Community Status: 2013
Phosphorus in the Great Lakes:
Advanced Ecology Option C.
TOWARDS THE GOAL OF SETTING NUTRIENT CRITERIA FOR THE DELAWARE ESTUARY
Please fill in the questions on your entrance slip.
Topic 4.4: Water Pollution
Nutrient Cycles.
Presentation transcript:

Evaluating Phosphorus Limitation from the Maumee and Sandusky Rivers into Lake Erie Heather R. Kirkpatrick, Curtis C. Clevinger, Moumita M. Moitra, Darren L. Bade, Joseph D. Conroy, David A. Culver, William J. Edwards, Douglas D. Kane

Lake Erie & Eutrophication 1960’s: Harmful Algal Blooms (HABs); extreme eutrophication; hypolimnetic hypoxia 1972: Great Lakes Water Quality Agreement (GLWQA) signed; reduced phosphorus (P) entering Lake Erie; P detergents banned Late 1970’s-1980’s: Reductions in P recorded; decreased HABs and hypoxia Mid-1990’s: re-eutrophication of Lake Erie; increases in dissolved P; return of HABs and hypoxia Sandusky Bay in April (OhioLink Landsat 7)

P-limitation Paradigm P is considered most often limiting in freshwater Nitrogen fixation should reduce the occurrence of N limitation Managing for N may favor N limitation and N fixing cyanobacteria

P-limitation Demand of P by algae exceeds supply  Other factors are not limiting When P supply > demand  Another factor is limiting

Overall Project Goals To directly assess the role of P in facilitating HABs by determining: 1. How Microcystis uses the bioavailable portion of the total P? 2. Where in these systems blooms are triggered (upstream, nearshore or offshore)?

Specific Project Goals To assess conditions of P-limitation by determining: 1. Where and when does P-limitation occur? 2. What are the causes and consequences of P-limitation (or lack thereof)?

Methods Algal Phosphorus Debt (P-debt): - Amount of phosphate incorporated in 24 hours in dark - The more “phosphate starved” algae are the more phosphate is taken up - Scaled to algal biomass - Values above µmol P/ µg chl are considered P limited Phosphate Turnover Time (P-turnover): - Fast turnover times (less than 60 minutes) indicate P- limitation - Fast turnover times could be caused by a small phosphate pool or high demand by algae Healey & Hendzel 1979 Heath, R.T. 1986

Methods Chlorophyll a Secchi depth Total phosphorus Nitrate Ammonia

Sandusky System Results

Indicates agreement with P-turnover data LIMITED NOT LIMITED

Maumee System Results

Indicates agreement with P-turnover data LIMITED NOT LIMITED

Summary Sandusky system limited in 40% of the samples Maumee system limited in 70% of the samples Lake and tributary sites variable Sandusky Bay generally not P-limited Maumee River generally not P-limited

Summary Periods of high chlorophyll and low nitrate concentrations at Sandusky Bay and Maumee River sites Since P is generally not limiting at these sites, other factors (e.g. nitrogen) may be limiting

Conclusions P-limitation not ubiquitous Nitrogen may also be important in limiting algal growth Although we have potential nitrogen limitation, most cyanobacteria were not N fixing Management considering multiple factors may be more successful

Acknowledgements Funding: Lake Erie Protection Fund The Ohio Academy of Science Field collection crew Joshua Smith Dominique Guyton

LIMITED NOT LIMITED

LIMITED