Thomas Kiran M1, Archana Tiwari1 & M.V. Bhaskar2

Slides:



Advertisements
Similar presentations
Unit 1 Ecosystems Cycles of Matter.
Advertisements

Lesson Overview 3.4 Cycles of Matter.
Ecosystem Ecology. Serengeti at Sunrise Biogeochemistry.
Cycles in Matter Chapter 3.4.
Nutrient Cycles Eutrophication Nitrogen –Chemical Forms in the Aquatic Environment –Chemical Transformations –Cycle f-ratio Carbon.
How Human Activities Can Affect Sustainability Section 7.3
CHAPTER 54 ECOSYSTEMS Copyright © 2002 Pearson Education, Inc., publishing as Benjamin Cummings Section B: Primary Production in Ecosystems 1.An ecosystem’s.
Coastal Wetlands Land areas covered by salt water at least part of the year are called coastal wetlands Provide habitat and nesting for fish and wildlife.
Waste water treatment - Phycoremediation
5.4 EUTROPHICATION Connor. What is it?  excessive richness of nutrients (especially phosphates and nitrates) in a lake or other body of water, frequently.
Biogeochemical Cycles. There are 94 elements that are naturally occurring Most of them find their way into biotic systems in some way However it is important.
Electricity Part 4: Power Plants, Distribution and Cooling,
The Necessities of Life
Ahmed Atta A Introduction  Algae are a diverse group of primarily aquatic, single celled, plant like organisms. Most algae have characteristics.
HUMAN IMPACTS: LAND USE. More land is needed to grow food, to build roads and factories, and even to provide parks and recreation areas. As the human.
CHEMICALS IN THE ENVIRONMENT. CHEMICALS CYCLE  Earth is a closed system – which means that all atoms on earth remain on earth, including carbon and nitrogen.
Scale up of Algae Biofuels: Challenges and Opportunities Christopher Harto Argonne National Laboratory.
SA Populations of Lynx and Hare in Ontario. Environmental Systems and Ecosystem Ecology.
 Diatom forms gametes (auxospore) that fuse to become a specialized cell which swells to the maximum (original) size for the species.  Then divides asexually.
Environmental Systems and Ecosystem Ecology. Photosynthesis.
Biogeochemical Cycles Biology 20. Chemicals Cycle Inorganic nutrients are cycles through natural ecosystems repeatedly. Biogeochemical cycles are the.
©MathScience Innovation Center Our Backyard Waterways : Eutrophication Presented by: Rachel Martin Day 2.
Growing Algae for Biofuel Søren Laurentius Nielsen Department of Environmental, Social and Spatial Change.
Lesson Overview Lesson Overview Cycles of Matter Lesson Overview 3.4 Cycles of Matter.
Lesson Overview 3.4 Cycles of Matter.
Eutrophication Manish Kr. Semwal GMIS, Jakarta. Definition Eutrophication is a process whereby water bodies, such as lakes, estuaries, or slow-moving.
By: Jimmy and Kyle. Geological Features of Lakes  Oligotrophic lakes have less surface area relative to depth than eutrophic lakes.  Oligotrophic lakes.
Biogeochemical Cycles CP Environmental Science. Biogeochemical Cycles The chemical interactions that exist between the atmosphere, hydrosphere, geosphere,
What is a renewable energy? -Resource that can be replenished rapidly through natural processes as long as it is not used up faster than it is replaced.
CHEMICALS IN THE ENVIRONMENT. CHEMICALS CYCLE  Earth is a closed system – which means that all atoms on earth remain on earth, including carbon and nitrogen.
Biogeochemical Cycles Cycling of Matter in Ecological Systems.
All Sewers Lead to the Ocean Exploring and Measuring Stormwater Quality SciREN Coast February 12, 2015 Kellen Lauer and Kathleen Onorevole.
Electricity Part 4: Power Plants, Distribution and Cooling,
Aquatic Biomes. Determined by Salt content Flow rate Size (sometimes) 2 major categories of aquatic biomes: Salt water system Freshwater.
NOVEMBER 28, 2016 T.O.C. Necessary Nutrients POST LAB
ECOSYSTEM ECOLOGY.
Chapter 7-2 Marine Ecosystems.
LT: Today I can apply scientific concepts to understand environmental issues by analyzing the author’s purpose in diagrams. What are natural resources.
ERT 468 SURFACE WATER Surface Water Sources and Quality
Lesson Overview 3.4 Cycles of Matter.
Primary Productivity.
Carbon, Nitrogen, & Water Cycles Guided Notes
EFFECT OF ALGAL BLOOM ON FRESHWATER ECOSYSTEMS
Madipakkam Lake Restoration Project (Date 10/11/2016 – 14/11/2016)
SF Bay Estuary Ecology Notes
Section 7.3 How Human Activities Can Affect Sustainability
4.1 Ecosystems Part 1 Unit Goals:
Cycling of Matter and Nutrient Cycles
Lect 02 Energy and Biomass.
Abiotic Factors Affecting Aquatic Systems
What are The Necessities of Life?
Cycling of matter Section 3.4. Cycling of matter Section 3.4.
A World of Water “Living in water”
Oceans.
Cycling of Matter and the Climate System
Aquatic Biodiversity Ch. 6, Part 1.
Nutrient Limitations.
Freshwater and Marine Ecosystems
7 Environmental Systems and Ecosystem Ecology Part B
BIOGEOCHEMISTRY Nitrogen Cycle Slide:
The Nitrogen Cycle The most complex cycle
Water Pollution Close to home….
Lesson 5: The Dead Zone Chemical Oceanography
Aquatic Ecosystems.
Impacting the Environment
Chapter 3 The Biosphere.
Biogeochemical Cycles
4 Ways Humans negatively impact the environment
The Cycle The most complex cycle
Algal Biofuels By: Audrey Rothenberg, Amaris Gilbert, Signe Berg, Cambria Boulanger-Jewell.
Presentation transcript:

Thomas Kiran M1, Archana Tiwari1 & M.V. Bhaskar2 A new novel solution to grow diatom algae in large natural water bodies and its impact on CO2 capture and fish growth Thomas Kiran M1, Archana Tiwari1 & M.V. Bhaskar2 1Noida International University, Greater Noida, India, 2Kadambari Consultants Pvt. Ltd., Hyderabad, India Description of the proposed technology: Our proposed technology harnesses the enormous potential of diatom algae in Sequestering large amounts of CO2 in open waters. If we can convert this diatom biomass to fish biomass as diatoms being the primary producers in the food chain, their biomass will be consumed by Zooplankton which are in turn consumed by fish so the carbon captured by diatoms will be incorporated in to fish biomass (Fig.1). We want to use open water bodies as majority of them are nutrient rich with sewage and agricultural runoff. Blue green algae (BGA) which grow on top of the water layer stopping gaseous exchange and light which in turn stops other beneficial algae and aerobic bacteria to grow leading to hyper eutrophic condition. Diatoms which can dominate BGA in presence of sufficient silica concentration can help in BGA control and they can help in restoring the water quality by nutrient reduction, increase in fish biomass and enhanced oxygen production. Carbon in diatom biomass will be incorporated in to the food chain and the remaining biomass will rapidly settle to the bottom as diatom cells are made up of silica leading to efficient CCS. Limitations in Algae based Flue gas related CCS strategies: Relative large land area, Ability to capture only 25-30% CO2 in one go from flue gas, Cost of pumping flue gas and underdeveloped state of this technology (Benneman, 1993). 1MW power plant produces 2269 Metric tones of carbon which would require about 16 hectare algae bioreactor facility yielding 80g DW m-2 day-1 or 64 hectare algal facility yielding 20g DW m-2 day-1. Ability of algae to capture CO2 at fast rate to avoid acidification of medium resulting in culture crash is a main limiting factor in high CO2 sources like flue gas. Use of diatoms for CO2 sequestration: Diatoms being most productive and more diverse have distinctive advantage over other algal species studied for CO2 sequestration. Diatoms are largely responsible for CO2 export to ocean depths. Diatom cell membrane is highly permeable to CO2 resulting in efficient exchange between cell and external medium. Diatoms adapted to ambient high O2 and less CO2 concentration over geological times by the evolution of efficient carbon concentrating mechanisms (CCM). CCM helps diatoms concentrate CO2 at the site of fixation by RubisCO for better utilization. It is not exaggeration to believe that today’s atmospheric CO2 concentration is largely influenced by efficiency of diatom CCM (Hopkinson,2010). Diatom because of their silica cell wall exhibit very fast sinking rates compared to other algae. Diatoms with its efficient CCM which can work even at low DIC levels are the only competitors which can compete with BGA for nutrients if sufficient Si is present. Of the 10 ocean fertilization experiments 9 resulted in phytoplankton blooms dominated by diatoms (Smetacek, 2008) So diatoms respond very well to changes in nutrient concentration and grow rapidly even in open waters. Fig.1. Schematic diagram showing the mechanism of CO2 sequestration from diatom algae triggered by Nualgi. Advantages of diatoms over other algae: Diatoms are among most productive and environmentally diverse on planet. They are estimated to be responsible for 40% of global carbon fixation. They are highly diverse with estimates of over 100,000 species. According to Aquatic species program recommended list of most promising species for biofuel production, 60% of selected strains are diatoms. This list is based on high growth rate, lipid yield, tolerance to harsh environment and performance in mass scale. Diatoms have shown greater carbon fixing ability than other co existing algae per unit of crop carbon. Diatoms can even dominate under nutrient and light limited conditions. In spite of having all these advantages over other algal species it is quite puzzling that diatoms are the least explored species in the fields of algal biofuels and CO2 sequestration. Lab scale experimental data on growing diatom consortium using Nualgi in waste water: Fig.2. Effect of Nualgi on growth and lipid productivity of diatom consortium grown in waste water Mechanism to trigger diatoms in open waters: Growing one type of algae in open waters is complicated process but diatoms have a distinctive advantage because of their absolute requirement for silica. So using this advantage we can trigger diatoms in open waters especially in fresh water ecosystem were silica concentration is less. Taking this advantage in to consideration we have developed a nano silica based micronutrient mixture called “Nualgi” which has Nano silica as its major constituent along with iron and 9 other trace metals. The silica becomes both the carrier for other nutrients and the nutrient by itself. It is in a water dispersible particulate form. Nualgi because of its nano size is able to pervade very small spaces in the subsurface and remain suspended in water, there by increasing the bioavailability of the nutrients for easy absorption by micro algae and achieve wider distribution. In water Nualgi causes Diatom Algae to bloom, though any pond, lake, estuary or coastal water has many species of algae, only Diatoms require silica and they consume Nualgi rapidly and bloom. In lab experiments with pure marine diatom cultures highest biomass concentration and biomass productivity was attained in both C. clostridium and C. fusiformis in cultures grown in Nualgi containing medium these values were almost double than in the popular f/2 medium (Suman etal,2012). Fig.3. Effect of Diatom growth on physiochemical parameters of waste water In Orissa there are many water bodies like reservoir of Hirakud dam, Mahanadi river, Chilika lake, Bay of Bengal and water bodies in the vicinity of NALCO can be used to grow algae. Sewage released in to Mahanadi River from Cuttack is 172 MLD so by growing algae in these large water bodies and sea shores adjacent to big cities we can utilized these excess nutrients. Conclusion: For algae to be used as a carbon capture technology and energy alternative the process must be able to compete on a cost basis with other chemical and geological technologies. It should also be sustainable and if deployed global scale the land and water use must be minimized to preserve nature and to eliminate conflict over these resources with other users. Current CCS technologies are energy intensive and expensive often requiring optimized and controlled conditions. By using large water bodies which are nutrient rich to sequester CO2 using algae which are well adapted for efficient CO2 sequestration can emerge as a sustainable alternative to available technologies. The proposed technology has potential for future research, which may assist in the remediation of problems associated with water pollution and green house gases. Acknowledgements: We acknowledge Dr.S.Shivaji, Retd Scientist, CCMB, Hyderabad., Dr.D.V.Subba rao, Emeritus Scientist, Bedford Institute of oceanography, Dartmouth, Canada., Mr. Sampath kumar, Inventor, Nualgi , Bangalore. Carbon sequestration seminar 2015, Bhubaneswar, India.