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Ramin Yazdani. Quantifying Factors Limiting Aerobic Degradation During Aerobic Bioreactor ... PDF

127 Pages·2010·0.86 MB·English
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Quantifying Factors Limiting Aerobic Degradation During Aerobic Bioreactor Landfilling and Performance Evaluation of a Landfill-Based Anaerobic Composting Digester for Energy Recovery and Compost Production By RAMIN YAZDANI B.S. (California Polytechnic State University) 1986 M.S. (University of California-Davis) 1988 DISSERTATION Submitted in partial satisfaction of the requirements for the degree of DOCTOR OF PHILOSOPHY in Civil & Environmental Engineering in the OFFICE OF GRADUATE STUDIES of the UNIVERSITY OF CALIFORNIA DAVIS Approved: __________________________________________ George Tchobanoglous, Chair __________________________________________ Masoud Kayhanian __________________________________________ Jeannie Darby Committee in Charge 2010 -i- To my wife and children To my parents, sister, and grandparents “From cane reeds, sugar. From a worm's cocoon, silk. Be patient if you can, and from sour grapes will come something sweet.” By Jalaluddin Rumi -ii- ABSTRACT In the first part of the study, a bioreactor landfill cell was operated aerobically for six months to quantify the extent of aerobic degradation and mechanisms limiting aerobic activity during air injection and liquid addition. From an analysis of in situ aerobic respiration and gas tracer data, it was found that a large fraction of the gas filled pore space was in immobile zones where it was difficult to maintain aerobic conditions, even at relatively moderate landfill cell- average moisture contents of 33-36%. Even with the intentional injection of air, anaerobic activity was never less than 13%, and sometimes exceeded 65%. Analyses of gas tracer and respiration data were used to quantify rates of respiration and rates of mass transfer to immobile gas zones. The similarity of these rates indicated that waste degradation was influenced significantly by rates of oxygen transfer to immobile gas zones, which comprised 32 to 92% of the gas-filled pore space. In the second part of the study, a landfilled-based two-stage (anaerobic/aerobic) batch digester cell was constructed, operated, and monitored for treatment of source separated green waste while recovering energy and compost. The performance of this unique two-stage batch digester was evaluated in terms of cell operating temperature, leachate quality, methane generation rate, air emissions, waste decomposition indicators, energy production, and compost quality. The overall average temperatures of the cell -iii- during the anaerobic and aerobic phases were desirably high, in the thermophilic range. Although concentration of ammonia reached a high value of 2,400 mg/L, the volatile fatty acids concentrations and pH values were consistent with a healthy digester with no inhibition of methane production throughout the operating period. The decay rate observed in the landfill digester (k = 0.82/yr) thus represents about a 20-fold acceleration of methane generation compared to the U.S. EPA default for solid waste. The biofilter’s removal of volatile organic compounds and total gaseous non-methane organic compounds varied from 99 to 96% and 99 to 68%, respectively. The biochemical methane potential decreased by 83% during the entire operation, indicating compost feedstock contents were well decomposed. Compost removed and tested passed all of the U.S. Composting Council’s Seal of Testing Approval Standards. -iv- ACKNOWLEDGMENTS I would like to thank all of the people who guided and supported me through this long journey. First, I would like to express my sincere appreciation to my major professor, Dr. George Tchobanoglous, for his contributions and advice. He has been an inspiration and a source of encouragement and support during my graduate research work. I am grateful to Dr. Masoud Kayhanian for his support, technical review and valuable suggestions. My heartfelt thanks to Dr. Jeannie Darby, for her guidance and advice. Second, I am grateful to Mr. Don Augenstein for helping fund portion of the aerobic bioreactor landfill research work through funds from DOE-NETL. I am grateful for all of our lengthy creative discussions, from which I received diligent advice on improving my research work. Third, I would also like to thank Dr. Paul Imhoff and Dr. Pei Chiu at the University of Delaware for their valuable and creative contributions towards the aerobic bioreactor research. I would also like to thank Dr. Byunghyun Han and M. Erfan Mostafid for their valuable contributions. Fourth, I am also grateful to Dr. Morton Barlaz at the North Carolina State University for his contributions towards the anaerobic composting digester project. His collaboration in laboratory testing, insightful observation during -v- operations and monitoring, and many other constructive ideas improved the results of this research project. It was a pleasure working with him and I continue to appreciate his valuable input. Fifth, I am grateful to the funding agencies that made it possible to conduct this research, namely: California Department of Resources Recycling and Recovery (CalRecyle); U.S. Department of Energy-NETL; and the Yolo County. I would like to give a sincere thanks to Scott Walker with CalRecycle who was instrumental in funding these projects. I would also like to thank my employer, Yolo County, for their continued support during my graduate studies. The generous support of Environmental Research and Education Foundation scholarship for my doctorate degree is acknowledged and gratefully appreciated. Finally, I would like to thank my parents and other family members that have supported me through the many years I have been working on this degree. I would like to thank my wife, Becca for her love and support and our son, Dara, and daughter, Eilis, who have endured my many hours and years of graduate work and have encouraged me to finish. I dedicate this work to everyone in my family for being by my side and supporting and loving me unconditionally. I could have not done this without the love and support of everyone. I dedicate this to work to you all. -vi- CONTENTS Page ABSTRACT……………………………………………………………………….. iii ACKNOWLEDGMENTS………………………………………………………….v LIST OF FIGURES………………………………………………………………. x LIST OF TABLES………………………………………………………………… xiii DISSERTATION OVERVIEW…………………………………………………... 1 CHAPTER 1- Quantifying Factors Limiting Aerobic Degradation During Aerobic Bioreactor Landfilling 1.0 ABSTRACT…………………………………………………………………. 6 1.1 INTRODUCTION…………………………………………………………… 7 1.2 MATERIALS AND METHODS……………………………………………. 10 1.2.1 Landfill design and instrumention………………………………… 10 1.2.2 Landfill cell operation and testing………………………………… 13 1.2.3 In-situ aerobic respiration tests…………………………………… 15 1.2.4 Partitioning gas tracer tests……………………………………….. 15 1.3 RESULTS AND DISCUSSION………………………………………….... 17 1.3.1 Fluid pressure and gas composition……………………………... 17 1.3.2 In-situ aerobic respiration test results……………………………. 24 1.3.3 Partitioning gas tracer tests (PGTTs)……………………………. 25 1.4 FINDINGS….....…………………………………………………………….. 30 1.5 REFERENCES………………………………………………………………31 1.6 APPENDIX A……………………………………………………………….. 34 CHAPTER 2 – Performance Evaluation of a Landfill-Based Anaerobic Composting Digester for Energy Recovery and Compost Production 2.0 ABSTRACT…………………………………………………………………. 56 2.1 INTRODUCTION…………………………………………………………… 58 -vii- 2.2 MATERIALS AND METHODS……………………………………………. 61 2.2.1 Design and operation……………………………………………… 61 2.2.2 Monitoring and data analysis……………………………………… 67 2.2.2.1 Waste temperature monitoring………………………… 67 2.2.2.2 Leachate quality data and analysis…………………….67 2.2.2.3 Gas rate and characteristics…………………………… 68 2.2.2.3.1 Anaerobic phase methane generation rate…………………………….. 68 2.2.2.3.2 Aerobic phase gas testing and emissions……………………………... 70 2.2.2.4 Waste decomposition and related indicators Monitoring………………………………………………... 73 2.2.2.4.1 Biochemical methane potential, cellulose, hemicellulose, and moisture content………………………….. 74 2.2.2.4.2 Compost quality…………………………… 75 2.2.2.5 Net energy production measurement and calculation. 77 2.3 RESULTS AND DISCUSSION…………………………………………… 79 2.3.1 Waste temperature during filling, anaerobic phase and aerobic phase………………………………………………………. 79 2.3.2 Leachate quality……………………………………………………. 82 2.3.3 Methane generation rate and composition………………………. 86 2.3.4 Biofilter treatment efficiency……………………………………… 88 2.3.5 Indicator parameters for waste decomposition and product Stability……………………………………………………………… 92 2.3.6 Moisture balance during anaerobic and aerobic phase………... 95 2.3.7 Compost quality…………………………………………………….. 97 2.3.7.1 Physical characteristics of compost…………………… 97 2.3.7.2 Chemical characteristics of compost………………….. 103 2.3.7.3 Biological characteristics of compost…………………. 106 2.3.7 Overall net energy balance………………………………………...107 -viii- 2.4 FINDINGS…………………………………………………………………... 108 2.6 REFERENCES………………………………………………………………110 -ix- LIST OF FIGURES Figure 1.1: Cross sectional view of Yolo County aerobic bioreactor landfill cell illustrating the location of instrumentation, gas collection and leachate recirculation lines, respiration tests locations, and partitioning gas tracer tests…………………………………………..11 Figure 1.2: Percent anaerobic activity and total fluid pressure in instrumentation layers 1 and 2. Measurements reported for layer 1 and 2 are averages of all readings in each layer. Periods when the blower was off for longer than 2 days are indicated……………….14 Figure 1.3: Contours of gas composition in layer 1 on 8/23/06. Solid lines correspond to outline of landfill. (a) Percent anaerobic activity. Dashed lines represent regions where P ≥ 50% and dotted lines where P < 50%. (b). Oxygen concentration. Dashed lines represent regions where oxygen concentration < 10%. (c) Waste temperature. Dashed lines represent regions where landfill temperature > 70°C………………………………………………………………….... 23 Figure 1.4: Data from in-situ respiration tests in aerobic bioreactor landfill cell……………………………………………………………………... 25 Figure A1(a): Plan view of aerobic landfill cell…………………………………….. 35 Figure A1(b): Schematic of total fluid pressure measurement and vertical cross- section…………………………………………………………………. 35 Figure A2(a): Cumulative supplemental liquid added and leachate recirculated during the operational periods……………………………………… 36 Figure A2(b): Cumulative gas flow exiting the landfill during the six month period when the landfill cell was operated as an aerobic bioreactor…… 37 Figure A3: Daily moving average gas flow rate during operation of aerobic bioreactor cell………………………………………………………….38 Figure A4: Variation of percent anaerobic activity, P, for the extreme case of 60% CH and 40%CO ……………………………………………….39 4 2 Figure A5: Variation of percent anaerobic activity, P, for the extreme case of 40% CH and 60% CO ……………………………………………... 40 4 2 Figure A6: Aerobic bioreactor cell moisture content based on EPA method (8) and total fluid pressure determined from bubble level monitor and LLDPE tubes in instrumentation layers 1 and 2. Measurements reported for layer 1 and 2 are averages of all readings in each -x-

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Jeannie Darby, for her guidance and advice. Second .. (translated to electricity production) was estimated at 46 kWh per Mg of wet . The horizontal leachate injection and recirculation piping used was 31.8 chloride (PVC) pipe.
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