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THE EFFECT OF PRETREATMENT METHODS ON METHANE YIELD AND NUTRIENT SOLUBILIZATION DURING ANAEROBIC DIGESTION OF MICROALGAE A Thesis presented to the Faculty of California Polytechnic State University, San Luis Obispo In Partial Fulfillment of the Requirements for the Degree Master of Science in Civil and Environmental Engineering by Alexander Scott Hill June 2014 © 2014 Alexander Scott Hill ALL RIGHTS RESERVED ii COMMITTEE MEMBERSHIP TITLE: The Effect of Pretreatment Methods on Methane Yield and Nutrient Solubilization During Anaerobic Digestion of Microalgae AUTHOR: Alexander Scott Hill DATE SUBMITTED: June 12, 2014 COMMITTEE CHAIR: Dr. Trygve Lundquist, Associate Professor Civil & Environmental Engineering Department COMMITTEE MEMBER: Dr. Yarrow Nelson, Professor Civil & Environmental Engineering Department COMMITTEE MEMBER: Dr. Gregory Schwartz, Assistant Professor Bioresource Agriculture Engineering Department iii ABSTRACT The Effect of Pretreatment Methods on Methane Yield and Nutrient Solubilization During Anaerobic Digestion of Microalgae Alexander Scott Hill Microalgal biomass is a candidate feedstock for biofuel production. To improve the sustainability of algae biofuel production, following biofuel recovery, the biomass nutrients should be recycled for additional algae growth. Anaerobic digestion of algae or oil-extracted algae is a means of recovering carbon and other nutrients, while offsetting algae production electricity demand. The major limiting factor in microalgae digestion is the low biodegradability of the cell walls. In the present study, various pretreatment technologies were tested at bench scale for their ability to improve raw, non-lipid- extracted algae biodegradability, which was assessed in terms of methane yield, volatile solids destruction, and solubilization of N, P, and K. The microalgae were harvested by sedimentation from outdoor wastewater-fed raceways ponds operated in coastal southern California. Four pretreatment methods (sonication, high-pressure homogenization, autoclaving, and boiling) were used on the algae slurries, each followed by batch anaerobic digestion (40 days at 35oC). Biomass sonication for 10 minutes showed the highest methane yield of 0.315 L CH / g VS , which is a 28% increase over the 4 IN untreated control. Conversely, autoclaved algae slurry inhibited methane production (0.200 vs. 0.228 L CH / g VS for the treatment and control). A preliminary energy 4 IN balance indicated that none of the pretreatments led to a net increase in energy conversion to biomethane. However, pretreatment did increase the initial N and P solubilization rates, but, after digestion, the ultimate N and P solubilization was nearly the same among the treatments and controls. After 40 days of digestion, solubilization of N, P, and K iv reached, respectively, 50-60% of average total Kjeldahl N, 40-50% of average total P, and 80-90% of average total K. Descriptive first-order models of solubilization were developed. Overall, certain pretreatments marginally improved methane yield and nutrient solubilization rate, which cast doubt on the efficacy of, or even the need for, algae biomass pretreatment prior to anaerobic digestion. Keywords: batch anaerobic digestion, pretreatment, solubilization, digestate, NPK, lysis, sonication, high pressure homogenization, heat treatment, L CH /g VS 4 IN v ACKNOWLEDGMENTS I would like to thank: My Parents for their support Kaylinn for putting up with my antics…although it doesn’t end here! Trygve Lundquist for his guidance Greg Schwartz for his support and enthusiasm Yarrow Nelson for his diligence in reviewing my thesis Ruth Spierling for her wholehearted commitment to the end goal and relentless desire to improve me as a scientist and engineer Matt Hutton for is insightful knowledge of the project, the real world, obscure mountain adventures, and Internet sensations Braden Crowe for his dedication to San Clemente Mike Chang, Justin Kraetsch, Eric Nicolai, Chad Boggess, and Nate Olivas, for trudging through this together Perry Ng for his mastery of the total phosphorus test Serena Lee for her statistical help Amy and Kay for their administrative guidance Shelley Blackwell for her commitment to the logistical nature of the project All of the ENVE 405 helpers directly involved in my project: Chris Apple, Paul Camarena, David Sng, Cameron Whipple, James Pilkington, Krissy Stroud, Elai Fresco, Christian Bowen, Anne Guzman, as well as all of the additional help I was fortunate to glean from the massive organized band of interdisciplinary wonder The Department of Energy for funding such an exciting project vi Table of Contents List of Tables ...................................................................................................................... x List of Figures ................................................................................................................... xv List of Equations ............................................................................................................. xxv 1 Introduction ................................................................................................................. 1 2 Background ................................................................................................................. 4 2.1 Anaerobic Digestion ........................................................................................... 4 2.2 Benefits of Microalgae for Biofuel Production .................................................. 5 2.3 Historical Experiments Involving Anaerobic Digestion of Microalgae ............. 6 2.4 Anaerobic Digestion Enhancement ..................................................................... 6 2.5 Nutrient Recycling .............................................................................................. 8 2.6 Variables Affecting Anaerobic Digestion of Microalgae ................................. 10 2.7 Rationale of the Present Study .......................................................................... 11 3 Methods..................................................................................................................... 13 3.1 Overview of Experiments ................................................................................. 13 3.1.1 Collection and Storage of Algae ............................................................... 15 3.1.2 Collection and Storage of Digester Inoculum ........................................... 18 3.1.3 Sonication ................................................................................................. 19 3.1.4 High Pressure Homogenization ................................................................ 20 3.1.5 Autoclaving ............................................................................................... 23 vii 3.1.6 Boiling....................................................................................................... 24 3.2 Digester Setup ................................................................................................... 25 3.2.1 Experimental Overview and Sample Identification .................................. 28 3.3 Analytical Procedures ....................................................................................... 30 3.3.1 Overview of Sample Day Breakdown ...................................................... 30 3.3.2 Solids Concentration ................................................................................. 32 3.3.3 Biogas Volume and Composition ............................................................. 32 3.3.4 Chemical Oxygen Demand (COD) Determination ................................... 34 3.3.5 pH/Alkalinity Determination .................................................................... 36 3.3.6 Nitrogen Determination ............................................................................ 36 3.3.7 Phosphorus Determination ........................................................................ 38 3.3.8 Potassium Determination .......................................................................... 40 4 Results and Discussion ............................................................................................. 41 4.1 Effect of Pretreatment on Methane Yield and Nutrient Solubilization............. 41 4.1.1 Degree of Cell Disruption ......................................................................... 42 4.1.2 Specific Methane Yield............................................................................. 46 4.1.3 Net Energy Balance .................................................................................. 50 4.1.4 Effect of Organic Loading on Degradation Rate ...................................... 54 4.1.5 Neutral to Negative Effects of High Heat on Biodegradability ................ 57 4.1.6 Nitrogen Solubilization ............................................................................. 59 viii 4.1.7 Phosphorus Solubilization ........................................................................ 65 4.1.8 Potassium Solubilization ........................................................................... 76 4.2 Descriptive Modeling........................................................................................ 77 4.2.1 TAN Model Generation ............................................................................ 78 4.2.2 DRP Model Generation............................................................................. 81 5 Conclusions ............................................................................................................... 84 5.1 Pretreatment Effect on Specific Methane Yield ............................................... 84 5.2 Pretreatment Effect on Nutrient Solubilization ................................................. 85 5.2.1 Nitrogen Solubilization ............................................................................. 85 5.2.2 Phosphorus Solubilization ........................................................................ 85 5.2.3 Potassium Solubilization ........................................................................... 86 5.3 Model Creation ................................................................................................. 86 5.4 Limitations of the Study.................................................................................... 87 5.5 Future Research ................................................................................................ 87 6 Works Cited .............................................................................................................. 90 7 Appendices ................................................................................................................ 95 ix List of Tables Table 1. Partial list of various pretreatment technologies that have been applied to increase biogas yields of anaerobic digestion of microalgae. ................................. 7 Table 2. The methane yield and TAN concentrations were normalized by initial volatile solids. Source: (Sialve B., 2009) .............................................................. 10 Table 3. Overview of all five experiments and their respective logistical information. ........................................................................................................... 15 Table 4. Analytical tests and the corresponding stage during experimental setup at which point the samples were pulled. The orange markers relate to when the samples were pulled as seen in Figure 14. ..................................................... 27 Table 5. Overview of all five experiments and their respective sample identification. TS in experiment 3 refers to “total solids.” ................................... 29 Table 6. Analytical procedures that were performed in order to track digester health, biogas production, and nutrient release. The third party laboratory used for the potassium testing was the U.C. Davis Analytical Laboratory. ......... 30 Table 7. Summary of pretreatment methods and means of cell disruption ...................... 41 Table 8. Comparison of the degree of cell disruption by various pretreatments, based on soluble COD release. All untreated samples had a sCOD/tCOD ratio of 3-5% (not shown). .................................................................................... 44 Table 9. Comparison of specific methane yields of all five experiments. Values highlighted in yellow were extrapolated from data (see explanation below). Sample coding is explained by the blue headers. UAS means untreated sample. The culture volumes were either 125 mL or 1.2 L and x

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to biomethane. However, pretreatment did increase the initial N and P solubilization rates adventures, and Internet sensations. Braden Crowe for .. Untreated algae + seed for the boiled experiment did not have enough sample
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