Use of Algae Reactors to Remediate Eutrophication in the Mississippi River Delta Brendan Scott Joseph Vassios BZ 572 November 9, 2010.

Slides:



Advertisements
Similar presentations
AP Environmental Science Earth’s Environmental Systems
Advertisements

Overview – Nutrient Fate and Transport Mark B. David University of Illinois at Urbana-Champaign Presented at Building Science Assessments for State-Level.
AP Environmental Science Chapters 17 and 18. * Eutrophic Lake.
Net Environmental Benefit – Life Cycle Assessment of Algaculture at Wastewater Treatment Plants In this study, the net environmental benefit life cycle.
Syllabus statements: Chapter Video Labs:
INVESTIGATION OF BIOLOGICAL PHOSPHORUS REMOVAL IN A SEQUENCING BATCH REACTOR INVESTIGATION OF BIOLOGICAL PHOSPHORUS REMOVAL IN A SEQUENCING BATCH REACTOR.
Dr. Bajnóczy Gábor Tonkó Csilla WASTEWATERS CONTAINING PLANT NUTRIENTS BUDAPEST UNIVERSITY OF TECHNOLOGY AND ECONOMICS DEPARTMENT OF CHEMICAL AND ENVIRONMENTAL.
Nitrogen, Phosphorus, & Eutrophication
1. Review- By what two processes is water cycled from land to the atmosphere Sequence- Describe one way in which water from Lake Superior may make one.
Eutrophication of the Black Sea
Water Pollution and Treatment
Eutrophication comparisons between Chesapeake Bay and Puget Sound Tiffany Huang Oceanography 497 B School of Aquatics and Fisheries.
Assessing Aquatic Ecosystems & Measurement. Aquatic Ecosystem Assessment The health of an aquatic ecosystem can be determined by examining a variety of.
The Gulf of Mexico’s Hypoxic Zone
What caused these whales to die and wash ashore?
Eric G. Hurley, Nutrient Management Specialist USDA-Natural Resources Conservation Service.
Pomme de Terre Lake Water Quality Summary Pomme de Terre Lake Water Quality Summary US Army Corps of Engineers Environmental Resources Section.
Subjects – Energy Flow and Chemical Cycles – Photosynthesis and Respiration – Plant Processes Standards Next GenerationBiologyEnvironmental Modeling how.
WATER QUALITY. Sources of Water Pollution Water pollution results from some physical or chemical change that adversely affects human health or the health.
Nutrient Loading from Point and Non-Point Sources on Surface Waters by Adam Lanning.
All about “Dead Zones”. Zones of Oxygen Depletion.
Pollution of the Hydrosphere
Water Pollution.
Hypoxia in the Gulf of Mexico 07/03/2002.  Eutrophication is a natural process taking place in water- characterized by a development towards an environment.
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.
KATLYND REESE AQUATIC ECOLOGY 9 NOVEMBER 2011 Hypoxia or “Dead Zones” in Aquatic Systems.
SA Populations of Lynx and Hare in Ontario. Environmental Systems and Ecosystem Ecology.
The Gulf of Mexico Hypoxia Zone:. Mississippi River Basin.
Environmental Systems and Ecosystem Ecology. Photosynthesis.
Nitrogen cycle Biogeochemistry October 17, 2005 Maria Moskalenko, Gretchen Miles, Emily Paduano, Jaconette Mirck Biogeochemistry October 17, 2005 Maria.
©MathScience Innovation Center Our Backyard Waterways : Eutrophication Presented by: Rachel Martin Day 2.
Emily Schweiss, Alex Birkley, Petr Carter, and Eric Hempelmen.
Water Pollution. Questions for Today: What are examples of point and nonpoint pollution sources for water? What are examples of point and nonpoint pollution.
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.
SOIL AND WATER QUALITY MONITORING TECHINIQUES Ramesh Kanwar Professor and Chair, Agricultural & Biosystems Engineering Department Iowa State University,
Eutrophication Manish Kr. Semwal GMIS, Jakarta. Definition Eutrophication is a process whereby water bodies, such as lakes, estuaries, or slow-moving.
Pg. 82 RTW: Break apart the word “biogeochemical”. What definition can you make for biogeochemical cycle? Objective: I will be able to diagram and explain.
Jonathan Burnett Jackie Comisso Travis Borrillo-Hutter Terra Michaels.
Lesson 1.5 Pg
Nutrient Cycles Environmental Science. A Generalized Cycle Materials often move between the regions of the earth- - Atmosphere - Hydrosphere - Lithosphere.
The Blue Planet The Blue Planet Indicators of Water Quality.
© SSER Ltd.. Green plants manufacture organic compounds such as carbohydrates, proteins and lipids by the process of photosynthesis The manufacture of.
POLLUTION MANAGEMENT 5.4 Eutrophication. Assessment Statements  Outline the processes of eutrophication.  Evaluate the impacts of eutrophication.
Chapter 22 Water Pollution
Water Quality Indicators & Water Pollution. EPA - Environmental Protection Agency  Government agency responsible for protecting human health and the.
 Salinity: Salinity is the concentration of dissolved salts in the water and is an important element of a  habitat. Aquatic animals are adapted to living.
BeforeAfter Eutrophication. Eutrophication – nutrient enrichment of waters Major nutrients -phosphorus and nitrogen Consequences -increased plant growth.
Water Pollution. Types of Water Pollution Point Source –From a single, traced source –Ex: drain pipes, effluent of sewage treatment Nonpoint Source –Scattered;
Introduction to Nutrient Management, Nutrient Cycling and Regional Nutrient Balance Issues Tom Basden Ag. and Natural Resources WVU Extension Service,
The Nitrogen Cycle. Why is nitrogen important? Its an essential part of many biological molecules. Proteins Nucleic acids (DNA) Chlorophyll Adenosine.
Vocabulary:  Eutrophication: is a natural process; where lakes, as they age, build up nutrients which cause phytoplankton to grow.  Phytoplankton: Microscopic.
Aquaponics for Sustainability Education
Watersheds Review Science 8 SOL.
EFFECT OF ALGAL BLOOM ON FRESHWATER ECOSYSTEMS
Manure 101 University of Wisconsin - Extension
Eutrophication & Management
Nitrogen and Phosphorus
Eutrophication & Management
Managing the Soil Section 4.2.
Human Effects on Hydrosphere Quality
ENVIRONMENTAL SYSTEMS
Eutrophication Nitrogen and Phosphorus are often limiting factors in plant growth. Therefore they are used in fertilizers to improve plant growth. However,
Environmental Systems
Water Pollution.
Human Effects on Hydrosphere Quality
Human Effects on Hydrosphere Quality
Eutrophication & Management
With your hosts, the Fabulous BTW Educators
Nutrient Cycles.
Presentation transcript:

Use of Algae Reactors to Remediate Eutrophication in the Mississippi River Delta Brendan Scott Joseph Vassios BZ 572 November 9, 2010

Mississippi River Basin 1.5 Million Square Miles

Ecology of Hypoxia

Introduction – Mississippi River  Increased fertilization and leaching of top soil has increased nitrogen concentrations in the Mississippi River and consequently the Gulf of Mexico  Increased concentrations of nitrogen has led to seasonal eutrophication of the Gulf of Mexico

Nitrogen  Nitrogen is used by plants for:  Nucleic acid (DNA & RNA)  Amino acids  Pigments  Eutrophication as a result of increased nitrogen can lead to:  Detrimental algae blooms  Reduced dissolved oxygen (hypoxia)  Fish kills

Nitrogen’s Role in Eutrophication

Current Regulation of Nitrogen  EPA limits for nitrogen in drinking water:  Nitrate – 10 ppm  Nitrite – 1 ppm  Ammonia – Varies  Total N – 11 ppm  Leaching from agricultural soils is currently unregulated

USGS, 2010

Nitrogen Levels Directly Proportional to Amount of Tile Farming USGS, 2010

Current Remediation Strategies  Current strategies incorporate mitigation by altering farming processes  Reduce nitrogen inputs  Crop rotation  Modified cultural practices  Previous research using algae for wastewater remediation (phytoaccumulation):  Algae turf scrubber  Algae biofilm

Algae Turf Scrubber

Algae Biofilm Qun et al., 2008

Algae Biofilm Qun et al., 2008

Potential Algae Species Anabaena cylindricaSpirogyra sp. obacteriaslides.shtml b20a.htm

Algae is also intentionally cultivated, supporting a multimillion dollar international industry

Design Criteria For Algae Reactor  Simple  Passive  Relatively efficient  Movable  Exploit a natural ecosystem  Turn a waste stream into energy

Palate sized for ease of transport with a footprint of 11 square feet Ergonomically accessible for reach with a height of 5 feet Effective surface area of 1320 square feet created by 120 trays spaced one ½ inch apart

Cheap durable construction materials Plexi glass for reactor housing Removable screens as scaffolding for algae

Hybridization of Existing Technologies

Wastewater Treatment Calculations Monod Growth Kinetics With variables of Influent Nitrogen Concentration Reactor Effluent Substrate Concentration Specific Growth Rate Hydraulic Retention Time S=K[(1+bθ)/(θ(Yq-b)-1)] Yielded reactor surface areas smaller than “Dead Zone”

Optimal Residence Time of 8 Days

Calculation Based on Equal Areas Area of “Dead Zone” 8000 square miles at peak Effective surface area of reactor 1320 Square feet Number of units required for total removal 169 million, Equivalent to 67 square miles of reactors 0.004% of farm land in Mississippi River basin

Moving Forward  Create working prototype  Trials with various algae species, light conditions, residence times  Test influent and effluent conditions over long time span  Test reactor algae as fertilizer or product stream  Determine economic viability of reactors  Conduct risk assessment and feasibility studies

Questions?

References  Size-Dependent Nitrogen Uptake in Micro and Macroalgae, M. Hein, Marine Ecology Press Series Vol. 118, 1995  Sources and Transportation of Nitrogen in the Mississippi River Basin, D. Goolsby, USGS  Phytoremediation as a Management Option for Contaminated Sediments in Tidal Marshes, V. Bert, Environmental Science Vol. 16, 2009  Nutrient Uptake in Streams Draining Agricultural Catchments of the Midwestern United States, M. Bernot, Fresh Water Biology Vol. 51, 2006  Nutrient Removal Potential of Selected Aquatic Macrophytes, K. Reddy, Journal of Environmental Quality Vol. 14, 1985  Nitrogen and Phosphorus Removal from Urban Wastewater by the Microalga Scendesmus obliquus, M. Martinez, Bioresource Technology, Vol. 73, 2000

 Nitrogen and Phosphorus in the Upper Mississippi River: Transport, Processing, and effects on the river ecosystem, J. Houser, Hydrobilogia Vol. 640, 2010  Nutrient Content of Seagrass and Epiphytes in the Northern Gulf of Mexico: Evidence of Phosphorus and Nitrogen Limitation, M. Johnson, Aquatic Botany Vol. 85, 2006  Reducing Hypoxia in the Gulf of Mexico: Advise from Three Models, D. Scavia, Estuaries Vol. 27, 2004  Limnology, Third Edition, R. Wetzel, Academic Press

 Ecological Stoichiometery in Freshwater Benthic Systems: Recent Progress and Perspectives, W. Cross, Freshwater Biology Vol. 50, 2009  Postaudit of Upper Mississippi River BOD/DO Model, W. Lung, ASCE  Environmental Biotechnology: Principals and Applications, P. McCarty, McGraw-Hill, 2001  An economic assessment of algal turf scrubber technology for treatment of dairy manure effluent, C. Pizarro, Biological Engineering Vol. 26, pg , 2006  Removing nitrogen and phosphorus from simulated wastewater using algal biofilm technique, W.E.I. Qun, Front. Environ. Sci. Engin. Vol. 2, pg , 2008  Nutrients in the Nation’s Streams and Groundwater, , Circular 1350, N. Dubrovsky, USGS, Accessed at: