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| Contents | ||||||
| Preface | v | |||||
| Contributors | xxiii | |||||
| 1 | Characteristics and Quantity of Biosolids | |||||
| Nazih K. Shammas and Lawrence K. Wang | 1 | |||||
| 1. | Introduction | 1 | ||||
| 2. | Primary Biosolids | 3 | ||||
| 2.1 | Estimation of Primary Biosolids Production | 3 | ||||
| 2.2 | Factors Affecting Solids Removal | 7 | ||||
| 2.3 | Composition and Characteristics of Primary Biosolids | 9 | ||||
| 3. | Biological Biosolids | 10 | ||||
| 3.1 | General Characteristics | 10 | ||||
| 3.2 | Activated Sludge | 10 | ||||
| 3.3 | Trickling Filter Biosolids | 22 | ||||
| 3.4 | Biosolids from Rotating Biological Contactors | 26 | ||||
| 3.5 | Coupled Attached-Suspended Growth Biosolids | 26 | ||||
| 3.6 | Denitrification Biosolids | 27 | ||||
| 4. | Chemical Biosolids | 27 | ||||
| 5. | Characteristics of Biosolids | 28 | ||||
| 5.1 | Specific Gravity and Volatility | 28 | ||||
| 5.2 | Preconcentration or Dewatering of Biosolids | 29 | ||||
| 5.3 | Particle Surface Charge and Hydration | 31 | ||||
| 5.4 | Particle Size | 32 | ||||
| 5.5 | Compressibility | 33 | ||||
| 5.6 | Biosolids Temperature | 34 | ||||
| 5.7 | Ratio of Volatile Solids to Fixed Solids | 34 | ||||
| 5.8 | Biosolids pH | 34 | ||||
| 5.9 | Septicity | 34 | ||||
| 5.10 | Trace Elements and Heavy Metals | 34 | ||||
| 6. | Examples | 35 | ||||
| 6.1 | Example 1: Determination of Biosolids Volume | 35 | ||||
| 6.2 | Example 2: Determination of Solids Content After Digestion | 36 | ||||
| 6.3 | Example 3: Determination of Biosolids Production | 36 | ||||
| 6.4 | Example 4: Interaction of Yield Calculations and the Quantitative Flow Diagram | 40 | ||||
| Nomenclature | 40 | |||||
| References | 41 | |||||
| 2 | Gravity Thickening | |||||
| Nazih K. Shammas and Lawrence K. Wang | 45 | |||||
| 1. | Introduction | 45 | ||||
| 1.1 | General | 45 | ||||
| 1.2 | Gravity-Thickening | 46 | ||||
| 1.3 | Process Evaluation | 46 | ||||
| 1.4 | Types and Occurrence of Thickening Processes | 47 | ||||
| 2. | Sedimentation Basins | 47 | ||||
| 2.1 | Primary Sedimentation | 47 | ||||
| 2.2 | Secondary Sedimentation | 47 | ||||
| 3. | Gravity Thickeners | 47 | ||||
| 3.1 | Introduction | 47 | ||||
| 3.2 | Theory | 48 | ||||
| 3.3 | System Design Considerations | 49 | ||||
| 4. | Cost | 55 | ||||
| 4.1 | Capital Cost | 55 | ||||
| 4.2 | Operating and Maintenance Cost | 55 | ||||
| 5. | Design of Thickeners | 56 | ||||
| 5.1 | Input Data | 57 | ||||
| 5.2 | Design Parameters | 58 | ||||
| 5.3 | Design Procedure | 59 | ||||
| 5.4 | Output Data | 61 | ||||
| 6. | Design Example 1 | 61 | ||||
| 6.1 | Thickener Surface Area | 61 | ||||
| 6.2 | Hydraulic Loading | 62 | ||||
| 6.3 | Torque Requirements | 62 | ||||
| 6.4 | Tank Depth | 62 | ||||
| 7. | Design Example 2 | 63 | ||||
| 7.1 | Quantity of Sludge and Solids | 63 | ||||
| 7.2 | Surface Area of Thickeners | 63 | ||||
| 7.3 | Diameter of Thickeners | 64 | ||||
| 8. | Design Example 3 | 64 | ||||
| 8.1 | Height of Sludge at the Required Solids Concentration (C") | 64 | ||||
| 8.2 | Surface Area of Thickener | 64 | ||||
| 8.3 | Solid Loading | 65 | ||||
| Nomenclature | 66 | |||||
| References | 66 | |||||
| Appendix | 69 | |||||
| 3 | Flotation Thickening | |||||
| Lawrence K. Wang, Nazih K. Shammas, William A. Selke, and Donald B. Aulenbach | 71 | |||||
| 1. | Introduction | 71 | ||||
| 1.1 | Flotation Processes | 71 | ||||
| 1.2 | DAF Thickener Components | 72 | ||||
| 1.3 | DAF Thickener Advantages and Disadvantages | 72 | ||||
| 2. | DAF Thickener Process Description | 73 | ||||
| 2.1 | Full presentation DAF-Thickening System | 74 | ||||
| 2.2 | Partial Pressurization DAF-Thickening System | 74 | ||||
| 2.3 | Recycle Pressurization DAF-Thickening System | 74 | ||||
| 3. | Process Applications and Limitations | 75 | ||||
| 3.1 | Sludge Thickening Applications | 76 | ||||
| 3.2 | DAF Thickening Process Limitations | 76 | ||||
| 4. | Process Design Considerations | 76 | ||||
| 4.1 | Rectangular or Circular Shape | 76 | ||||
| 4.2 | Concrete or Steel Construction | 76 | ||||
| 4.3 | Pilot-Scale or Bench-Scale Experiments | 78 | ||||
| 4.4 | Influent Feed Characteristics | 78 | ||||
| 4.5 | Thickener Surface Area | 79 | ||||
| 4.6 | Air-to-Solids Ratio | 81 | ||||
| 4.7 | Polymer Usage | 83 | ||||
| 4.8 | Pressurization System | 83 | ||||
| 4.9 | Operating Pressure | 83 | ||||
| 4.10 | Quantity of Pressurized Flow | 84 | ||||
| 4.11 | Number of Units | 84 | ||||
| 4.12 | Feed Sludge Line | 84 | ||||
| 4.13 | Thickened Sludge Removal | 84 | ||||
| 4.14 | Bottom Sludge Draw Off, Subnatant Line, Pressurized Flow Piping, and Controls | 84 | ||||
| 5. | Process Performance | 85 | ||||
| 5.1 | Performance Data | 85 | ||||
| 5.2 | Factors Affecting Performance | 85 | ||||
| 6. | Process Cost and Operation Considerations | 86 | ||||
| 6.1 | Capital Cost | 86 | ||||
| 6.2 | Operating and Maintenance Costs | 87 | ||||
| 7. | Process Reliability and Environmental Impact | 87 | ||||
| 7.1 | Reliability | 87 | ||||
| 7.2 | Environmental Impact | 87 | ||||
| 8. | Process Design Criteria and Procedures | 88 | ||||
| 8.1 | Design Criteria | 88 | ||||
| 8.2 | Input Data of DAF Thickener Design | 88 | ||||
| 8.3 | Design Parameters | 89 | ||||
| 8.4 | Design Procedure for DAF Thickener With No Recycle (Direct Pressurization) | 89 | ||||
| 8.5 | Design Procedures for DAF Thickener With Recycle | 90 | ||||
| 8.6 | Output Data of DAF Thickener Design | 91 | ||||
| 9. | Design and Application Examples | 91 | ||||
| 9.1 | Example 1. Design of a DAF Thickener With No Recycle | 91 | ||||
| 9.2 | Example 2. Design of a DAF Thickener With Recycle | 93 | ||||
| 9.3 | Example 3. Complete DAF Thickening System Design | 95 | ||||
| Nomenclature | 97 | |||||
| References | 97 | |||||
| Appendix | 100 | |||||
| 4 | Centrifugation Clarification and Thickening | |||||
| Lawrence K. Wang, Shoou-Yuh Chang, Yung-Tse Hung, H. S. Muralidhara, and Satya P. Chauhan | 101 | |||||
| 1. | Introduction | 101 | ||||
| 2. | Principles | 102 | ||||
| 3. | Types of Water Associated with Solid Particles | 102 | ||||
| 4. | Types of Centrifuges | 103 | ||||
| 4.1 | Basket Centrifuge | 103 | ||||
| 4.2 | Solid-Bowl Centrifuge | 104 | ||||
| 4.3 | Disc Centrifuge | 107 | ||||
| 5. | Performance of Centrifuges in Sludge Dewatering | 109 | ||||
| 5.1 | Separation of Municipal Wastewater Treatment Plant Sludges by Centrifugation | 109 | ||||
| 5.2 | Separation of Pulp and Paper Sludges by Centrifugation | 110 | ||||
| 5.3 | Separation of Electroplating by Centrifugation | 112 | ||||
| 5.4 | Separation of Coals and Refuse by Centrifugation | 114 | ||||
| 5.5 | Separation of Metallurgical Refinery Sludge by Centrifugation | 121 | ||||
| 5.6 | Separation of Cannery Waste Biological Sludge by Centrifugation | 122 | ||||
| 5.7 | Separation of Potato Wastes by Centrifugation | 122 | ||||
| 6. | Centrifugation Design Considerations | 122 | ||||
| 6.1 | General Guidelines for Selecting a Centrifuge for Sludge Dewatering | 122 | ||||
| 6.2 | Centrifuge Manufacturers | 123 | ||||
| 6.3 | Materials for Centrifuge Construction | 124 | ||||
| 6.4 | Advantages and Disadvantages of Centrifugation in Various Applications | 124 | ||||
| 6.5 | Design Criteria, Input Data, and Design Parameters | 125 | ||||
| 6.6 | Design Procedure | 125 | ||||
| 7. | Operation and Maintenance | 126 | ||||
| 7.1 | Troubleshooting | 126 | ||||
| 7.2 | Preventive Maintenance | 126 | ||||
| 7.3 | Noise and Odor Control | 128 | ||||
| 8. | Design and Practical Application Examples | 128 | ||||
| 8.1 | Example 1: Centrifugation System Design | 128 | ||||
| 8.2 | Example 2: Centrifugation System Chemical Requirements | 129 | ||||
| 8.3 | Example 3: Centrifugation System Cost Estimation | 129 | ||||
| 8.4 | Example 4: Centrifugation Case Study | 129 | ||||
| Nomenclature | 131 | |||||
| References | 132 | |||||
| 5 | Anaerobic Digestion | |||||
| Jerry R. Taricska, David A. Long, J. Paul Chen, Yung-Tse Hung, and Shuai-Wen Zou | 135 | |||||
| 1. | Introduction | 135 | ||||
| 2. | Theory | 136 | ||||
| 2.1 | Nature of organic Wastes | 136 | ||||
| 2.2 | Biochemistry and Microbiology of the Anaerobic Process | 137 | ||||
| 2.3 | Reactor Configurations | 138 | ||||
| 2.4 | Organic Loading Parameters | 140 | ||||
| 2.5 | Time and Temperature Relationships | 141 | ||||
| 2.6 | Nutrient Requirements | 142 | ||||
| 2.7 | Gas Production and Utilization | 142 | ||||
| 3. | Design Practice | 144 | ||||
| 3.1 | Anaerobic Treatability Studies | 144 | ||||
| 3.2 | Anaerobic Reactor Design and Sizing | 146 | ||||
| 3.3 | Tank Construction and System Components | 149 | ||||
| 3.4 | System Equipment and Appurtenances | 150 | ||||
| 3.5 | Gas Utilization | 159 | ||||
| 3.6 | Sludge Pumping and Piping Considerations | 160 | ||||
| 4. | Management of Digestion | 160 | ||||
| 4.1 | Control of Sludge Feed | 160 | ||||
| 4.2 | Withdrawal of Sludge and Supernatant | 161 | ||||
| 4.3 | Maintenance of Reactor Stability | 161 | ||||
| 4.4 | Digester Performance Criteria | 162 | ||||
| 5. | Capital and Operating Costs | 162 | ||||
| 5.1 | Generals | 162 | ||||
| 5.2 | Items Included in Cost Estimates | 162 | ||||
| 6. | Design Examples | 163 | ||||
| 6.1 | Example Using Standards Design | 163 | ||||
| 6.2 | Example Using Solids Loading Factor | 165 | ||||
| 6.3 | Example Using Modified Anaerobic Contact Process | 167 | ||||
| 7. | Recent Development in Anaerobic Process | 168 | ||||
| Nomenclature | 173 | |||||
| References | 173 | |||||
| 6 | Aerobic Digestion | |||||
| Nazih K. Shammas and Lawrence K. Wang | 177 | |||||
| 1. | Introduction | 177 | ||||
| 2. | Process Description | 178 | ||||
| 2.1 | Microbiology | 178 | ||||
| 2.2 | Advantages | 178 | ||||
| 2.3 | Disadvantages | 178 | ||||
| 3. | Process Variations | 179 | ||||
| 3.1 | Conventional Semibatch Operation | 179 | ||||
| 3.2 | Conventional Continuous Operation | 179 | ||||
| 3.3 | Autothermal Thermophilic Aerobic Digestion (Using Air) | 179 | ||||
| 3.4 | Autothermal Thermophilic Aerobic Digestion (Using Oxygen) | 181 | ||||
| 4. | Design Considerations | 181 | ||||
| 4.1 | Temperature | 181 | ||||
| 4.2 | Solids Reduction | 182 | ||||
| 4.3 | Oxygen Requirements | 183 | ||||
| 4.4 | Mixing | 184 | ||||
| 4.5 | pH Reduction | 184 | ||||
| 4.6 | Dewatering | 184 | ||||
| 5. | Process Performance | 185 | ||||
| 5.1 | Total Volatile Solids Reduction | 185 | ||||
| 5.2 | Supernatant Quality | 185 | ||||
| 6. | Process Design | 186 | ||||
| 6.1 | Input Data | 186 | ||||
| 6.2 | Design Parameters | 186 | ||||
| 6.3 | Design Procedure | 186 | ||||
| 6.4 | Output Data | 189 | ||||
| 7. | Cost | 189 | ||||
| 7.1 | Capital Cost | 189 | ||||
| 7.2 | Operation and Maintenance Cost | 190 | ||||
| 8. | Recent Developments and Summary | 191 | ||||
| 8.1 | Recent Developments | 191 | ||||
| 8.2 | Summary | 192 | ||||
| 9. | Design Examples | 193 | ||||
| 9.1 | Example 1 | 193 | ||||
| 9.2 | Example 2 | 195 | ||||
| Nomenclature | 199 | |||||
| References | 199 | |||||
| Appendix | 205 | |||||
| 7 | Lime Stabilization | |||||
| Clint Williford, Wei-Yin Chen, Nazih K. Shammas, and Lawrence K. Wang | 207 | |||||
| 1. | Introduction | 207 | ||||
| 2. | Process Description | 208 | ||||
| 2.1 | History | 208 | ||||
| 2.2 | Current Status and Regulations | 208 | ||||
| 2.3 | Applicability | 211 | ||||
| 2.4 | Theory of the Process | 212 | ||||
| 2.5 | Advantages and Disadvantages | 212 | ||||
| 2.6 | Environmental Impacts | 213 | ||||
| 3. | Design Criteria | 213 | ||||
| 4. | Process Performance | 217 | ||||
| 4.1 | Deodorization | 217 | ||||
| 4.2 | Pathogen Reduction | 218 | ||||
| 4.3 | Dewatering and Settling Characteristics | 219 | ||||
| 4.4 | Chemical Characteristics | 220 | ||||
| 5. | Process Design | 223 | ||||
| 5.1 | Design of Lime Handling Facilities | 223 | ||||
| 5.2 | Biosolids-Lime Mixing Tank Design | 228 | ||||
| 5.3 | PSRP Treatment to Meet Class B Requirements | 230 | ||||
| 5.4 | PFRP Treatment to Meet Class A Requirements | 231 | ||||
| 6. | Cost and Energy Usage | 232 | ||||
| 6.1 | Capital and Operating Costs | 232 | ||||
| 6.2 | Energy Usage | 234 | ||||
| 6.3 | Design Comparison for Lime-Only and Supplemental Heating Pasteurization | 234 | ||||
| 7. | Design Example | 235 | ||||
| 7.1 | Design Loading | 235 | ||||
| 7.2 | System Description | 236 | ||||
| 7.3 | Component Sizing | 237 | ||||
| Nomenclature | 238 | |||||
| References | 238 | |||||
| Appendix | 241 | |||||
| 8 | Pressurized Ozonation | |||||
| Lawrence K. Wang and Nazih K. Shammas | 243 | |||||
| 1. | Introduction | 243 | ||||
| 1.1 | Oxyozosynthesis Sludge Management System | 244 | ||||
| 1.2 | Oxyozosynthesis Wastewater Reclamation System | 247 | ||||
| 2. | Description of Processes | 249 | ||||
| 2.1 | Ozonation and Oxygenation Process | 249 | ||||
| 2.2 | Flotation Process | 251 | ||||
| 2.3 | Filter Belt Press | 255 | ||||
| 2.4 | Performance of Oxyozosynthesis Sludge Management System | 257 | ||||
| 2.5 | Performance of Oxyozosynthesis Wastewater Reclamation System | 259 | ||||
| 3. | Formation and Generation of Ozone | 260 | ||||
| 3.1 | Formation of Ozone | 260 | ||||
| 3.2 | Generation of Ozone | 261 | ||||
| 4. | Requirements for Ozonation Equipment | 264 | ||||
| 4.1 | Feed Gas Equipment | 264 | ||||
| 4.2 | Ozone Generators | 266 | ||||
| 4.3 | Ozone Contactors | 266 | ||||
| 5. | Properties of Ozone | 269 | ||||
| 6. | Disinfection by Ozone | 274 | ||||
| 7. | Oxidation by Ozone | 277 | ||||
| 7.1 | Ozone Reaction with Inorganics | 277 | ||||
| 7.2 | Ozone Reaction with Organic Material | 280 | ||||
| 8. | Oxygenation and Ozonation Systems | 285 | ||||
| 8.1 | Oxygenation Systems | 285 | ||||
| 8.2 | Ozonation Systems | 289 | ||||
| 8.3 | Removal of Pollutants from Waste by Ozonation | 291 | ||||
| Nomenclature | 291 | |||||
| Acknowledgments | 292 | |||||
| References | 292 | |||||
| 9 | Low-Temperature Thermal Treatment Processes | |||||
| Lawrence K. Wang, Clint Williford, Wei-Yin Chen, and Nazih K. Shammas | 299 | |||||
| 1. | Introduction | 299 | ||||
| 2. | Heat Conditioning Process | 299 | ||||
| 2.1 | Process Description | 299 | ||||
| 2.2 | Process Applications and Limitations | 300 | ||||
| 2.3 | Design Considerations | 301 | ||||
| 3. | Heat Drying Process | 304 | ||||
| 3.1 | Process Description | 304 | ||||
| 3.2 | Design Considerations | 305 | ||||
| 4. | Design and Application Examples | 309 | ||||
| 4.1 | Example 1 | 309 | ||||
| 4.2 | Example 2 | 314 | ||||
| 4.3 | Example 3 | 317 | ||||
| 4.4 | Example 4 | 320 | ||||
| 4.5 | Example 5 | 322 | ||||
| 4.6 | Example 6 | 324 | ||||
| 4.7 | Example 7 | 326 | ||||
| 4.8 | Example 8 | 326 | ||||
| 4.9 | Example 9 | 327 | ||||
| Nomenclature | 327 | |||||
| References | 328 | |||||
| 10 | Irradiation and Solid Substances Disinfection | |||||
| Lawrence K. Wang, J. Paul Chen, and Robert Ziegler | 331 | |||||
| 1. | Introduction | 331 | ||||
| 1.1 | Disinfection and Irradiation | 331 | ||||
| 1.2 | Pathogenic Organisms | 332 | ||||
| 1.3 | Pathogen Occurrence in the United States | 332 | ||||
| 1.4 | Potential Human Exposure to Pathogens | 332 | ||||
| 2. | Pathogens and Their Characteristics | 333 | ||||
| 2.1 | Viruses | 333 | ||||
| 2.2 | Bacteria | 334 | ||||
| 2.3 | Parasites | 334 | ||||
| 2.4 | Fungi | 336 | ||||
| 3. | Solid Substances Disinfection | 336 | ||||
| 3.1 | Long-Term Storage | 336 | ||||
| 3.2 | Chemical Disinfection | 336 | ||||
| 3.3 | Low Temperature Thermal Processes for Disinfection | 337 | ||||
| 3.4 | High Temperature Thermal Processes for Disinfection | 338 | ||||
| 3.5 | Composting | 338 | ||||
| 3.6 | High Energy Radiation | 339 | ||||
| 4. | Disinfection with Electron Irradiation | 339 | ||||
| 4.1 | Electron Irradiation Process Description | 340 | ||||
| 4.2 | Electron Irradiation Design Considerations | 341 | ||||
| 4.3 | Electron Irradiation Operational Considerations | 342 | ||||
| 4.4 | Electron Irradiation performance | 342 | ||||
| 5. | Disinfection with γ -Irradiation | 343 | ||||
| 5.1 | γ -Irradiation Systems | 343 | ||||
| 5.2 | γ -Irradiation Design Considerations | 346 | ||||
| 5.3 | γ -Irradiation Operational Considerations | 348 | ||||
| References | 349 | |||||
| 11 | Inorganic Chemical Conditioning and Stabilization | |||||
| Nazih K. Shammas and Lawrence K. Wang | 353 | |||||
| 1. | Introduction | 353 | ||||
| 2. | Factors Affecting Biosolids Conditioning | 354 | ||||
| 3. | Inorganic Chemical Conditioning | 356 | ||||
| 3.1 | Ferric Chloride | 356 | ||||
| 3.2 | Lime | 357 | ||||
| 3.3 | Dosage Requirements | 357 | ||||
| 3.4 | Other Types of Inorganic Conditioners | 357 | ||||
| 4. | Organic Polymers | 359 | ||||
| 5. | Selection of a Conditioning Chemical | 359 | ||||
| 5.1 | Jar Test | 359 | ||||
| 5.2 | Filter Leaf Testing | 360 | ||||
| 5.3 | Buchner Funnel Test for Determination of Specific Resistances | 362 | ||||
| 5.4 | Capillary Suction Time | 364 | ||||
| 6. | Cost | 364 | ||||
| 6.1 | Capital Cost | 364 | ||||
| 6.2 | Operation and Maintenance Cost | 365 | ||||
| 7. | Thermal Conditioning | 368 | ||||
| 7.1 | HT Process | 369 | ||||
| 7.2 | LPO Process | 370 | ||||
| 7.3 | Economic Considerations | 372 | ||||
| 7.4 | Advantages and Disadvantages of HT/LPO Conditioning | 372 | ||||
| 8. | Miscellaneous Conditioning Processes | 373 | ||||
| 8.1 | Elutriation | 373 | ||||
| 8.2 | Freeze-Thaw | 373 | ||||
| 8.3 | Mechanical Screening and Grinding | 374 | ||||
| 8.4 | Bacteria | 374 | ||||
| 8.5 | Electricity | 375 | ||||
| 8.6 | Solvent Extraction | 375 | ||||
| 8.7 | Ultrasonic | 375 | ||||
| 9. | Biosolids Stabilization | 375 | ||||
| 10. | Chlorine Stabilization | 376 | ||||
| 10.1 | Process Description | 376 | ||||
| 10.2 | Advantages and Disadvantages | 378 | ||||
| 10.3 | Chlorine Requirements | 379 | ||||
| 10.4 | Characteristics of Chlorine-Stabilized Materials | 380 | ||||
| 10.5 | Costs | 381 | ||||
| 11. | Design Example | 383 | ||||
| Nomenclature | 384 | |||||
| References | 384 | |||||
| Appendix | 388 | |||||
| 12 | Elutriation and Polymer Conditioning | |||||
| Lawrence K. Wang, Shoou-Yuh Chang, Yung-Tse Hung, and J. Paul Chen | 389 | |||||
| 1. | Elutriation Process Description | 389 | ||||
| 2. | Elutriation Process Design Considerations | 390 | ||||
| 2.1 | Reactor Design Considerations | 390 | ||||
| 2.2 | Elutriate Disposal Considerations | 391 | ||||
| 2.3 | New Technology Considerations | 391 | ||||
| 2.4 | Benefit | 392 | ||||
| 3. | Elutriation Process Design Procedures | 392 | ||||
| 3.1 | Multiple Elutriation in a Single Tank | 392 | ||||
| 3.2 | Countercurrent Elutriation in Multiple Tanks | 393 | ||||
| 4. | Chemical Conditioning with Soluble Organic and Inorganic Polymers | 394 | ||||
| 4.1 | Soluble Nonionic Organic Polymers | 394 | ||||
| 4.2 | Soluble Ionic Organic Polymers (Polyelectrolytes) | 394 | ||||
| 4.3 | Polyelectrolyte Conditioning Process for Sludge Thickening | 396 | ||||
| 4.4 | Polyelectrolyte Conditioning Process for Dewatering | 398 | ||||
| 4.5 | Inorganic Polymer Conditioning Process for Thickening and Dewatering | 399 | ||||
| 4.6 | Polyelectrolytes Determination and Process Control | 399 | ||||
| 5. | Design Examples | 399 | ||||
| 5.1 | Example 1 | 399 | ||||
| 5.2 | Example 2 | 400 | ||||
| 5.3 | Example 3 | 400 | ||||
| 5.4 | Example 4 | 400 | ||||
| Nomenclature | 401 | |||||
| Acknowledgments | 401 | |||||
| References | 401 | |||||
| 13 | Drying Beds | |||||
| Lawrence K. Wang, Y an Li, Nazih K. Shammas, and George P. Sakellaropoulos | 403 | |||||
| 1. | Introduction | 403 | ||||
| 2. | Sludge Drying Beds Process Description | 404 | ||||
| 2.1 | General Process Description | 404 | ||||
| 2.2 | Operation and Operating Variables | 406 | ||||
| 2.3 | Advantages and Disadvantages | 406 | ||||
| 3. | Types of Sludge Drying Beds | 407 | ||||
| 3.1 | Conventional Sand Drying Beds | 407 | ||||
| 3.2 | Paved Dying Beds | 408 | ||||
| 3.3 | Wedge-Wire Drying Beds | 408 | ||||
| 3.4 | Vacuum-Assisted Drying Beds | 409 | ||||
| 4. | Process Applications and Limitations | 410 | ||||
| 5. | Process Performance, Theory, and Principles | 410 | ||||
| 6. | Design Criteria, Requirements, and Other Considerations | 415 | ||||
| 6.1 | Land Requirements | 415 | ||||
| 6.2 | Covered Beds | 416 | ||||
| 6.3 | Sludge Conditioning | 416 | ||||
| 6.4 | Sludge Removal | 416 | ||||
| 6.5 | Sidestreams | 417 | ||||
| 6.6 | Bed Sizing Criteria | 417 | ||||
| 7. | Environmental Impact and Energy Consumption | 417 | ||||
| 8. | Cost | 420 | ||||
| 8.1 | Capital Costs | 420 | ||||
| 8.2 | Operating and Maintenance Cost | 420 | ||||
| 9. | Process Monitoring | 421 | ||||
| 10. | Design and Application Examples | 422 | ||||
| 10.1 | Example 1 | 422 | ||||
| 10.2 | Example 2 | 423 | ||||
| 10.3 | Example 3 | 427 | ||||
| 10.4 | Example 4 | 427 | ||||
| 10.5 | Example 5 | 427 | ||||
| Nomenclature | 428 | |||||
| References | 428 | |||||
| 14 | Animal Wastes Treatment Using Anaerobic Lagoons | |||||
| Lawrence K. Wang, Yung-Tse Hung, and J. Paul Chen | 431 | |||||
| 1. | Introduction | 431 | ||||
| 2. | Process Description | 432 | ||||
| 3. | Applications and Limitations | 432 | ||||
| 4. | Expected Process Performance and Reliability | 432 | ||||
| 5. | Process Design | 433 | ||||
| 5.1 | Minimum Treatment Volume | 433 | ||||
| 5.2 | Waste Volume for Treatment Period | 434 | ||||
| 5.3 | Sludge Volume | 436 | ||||
| 5.4 | Lagoon Volume Requirement | 436 | ||||
| 5.5 | Anaerobic Lagoons | 437 | ||||
| 5.6 | Data Gathering and Compilation for Design | 437 | ||||
| 6. | Energy Consumption and Costs of Anaerobic Lagoons | 440 | ||||
| 7. | Waste Storage Ponds | 441 | ||||
| 7.1 | Process Description | 441 | ||||
| 7.2 | Process Design | 441 | ||||
| 8. | Design and Application Examples | 443 | ||||
| 8.1 | Example 1 | 443 | ||||
| 8.2 | Example 2 | 443 | ||||
| 8.3 | Example 3 | 443 | ||||
| 8.4 | Example 4 | 445 | ||||
| 8.5 | Example 5 | 447 | ||||
| 8.6 | Example 6 | 448 | ||||
| 8.7 | Example 7 | 448 | ||||
| Nomenclature | 449 | |||||
| References | 449 | |||||
| 15 | Vertical Shaft Digestion, Flotation, and Biofiltration | |||||
| Lawrence K. Wang, Nazih K. Shammas, Jeffrey Guild, and David Pollock | 451 | |||||
| 1. | Introduction | 451 | ||||
| 1.1 | Biosolids Treatment | 451 | ||||
| 1.2 | VSB and VSD | 451 | ||||
| 1.3 | Vertical Shaft Flotation (VSF) Thickening Process | 453 | ||||
| 1.4 | Gas-Phase Biofiltration | 454 | ||||
| 1.5 | Biosolids Digestion and Stabilization | 454 | ||||
| 2. | Principles of Vertical Shaft Digestion (VSD) and Optional Anaerobic Digestion | 456 | ||||
| 2.1 | Theory and Principles of Aerobic Digestion | 456 | ||||
| 2.2 | Theory and Principles of Optional Anaerobic Digestion | 457 | ||||
| 2.3 | Combined VSD and Anaerobic Digestion | 458 | ||||
| 3. | Description, Operation, and Applications of VSD System | 458 | ||||
| 3.1 | Process Description | 458 | ||||
| 3.2 | Process Operation | 458 | ||||
| 3.3 | Process Applications | 459 | ||||
| 4. | Design Considerations of a Complete VSD System | 460 | ||||
| 4.1 | ATAD-Air | 460 | ||||
| 4.2 | ATAD-Oxygen | 461 | ||||
| 4.3 | Flotation Thickening After VSD | 462 | ||||
| 4.4 | Optional Dual Digestion System | 464 | ||||
| 4.5 | Biosolids Dewatering Processes | 465 | ||||
| 4.6 | Gas-Phase Biofiltration for Air Emission Control | 466 | ||||
| 4.7 | Operational Controls of Biofiltration | 469 | ||||
| 5. | Case Study | 470 | ||||
| 5.1 | Facility Design and Construction | 471 | ||||
| 5.2 | VSD Demonstration Plan | 473 | ||||
| 5.3 | Design Criteria Development for VSD | 475 | ||||
| 6. | Conclusions | 489 | ||||
| References | 489 | |||||
| Appendices | 493 | |||||
| 16 | Vacuum Filtration | |||||
| Nazih K. Shammas and Lawrence K. Wang | 495 | |||||
| 1. | Filtration Dewatering Systems | 495 | ||||
| 1.1 | Basic Theory | 496 | ||||
| 1.2 | Filter Aids | 496 | ||||
| 2. | Principles of Vacuum Filtration | 497 | ||||
| 3. | Application and Performance | 501 | ||||
| 4. | Auxiliary Equipment | 504 | ||||
| 5. | Operating Factors | 505 | ||||
| 5.1 | Machine Variables | 505 | ||||
| 5.2 | Filter Media | 505 | ||||
| 5.3 | Solids Feed Content | 506 | ||||
| 6. | Physical and Process Control | 507 | ||||
| 6.1 | Physical Control | 507 | ||||
| 6.2 | Process Control | 507 | ||||
| 7. | Upgrading Existing Units | 509 | ||||
| 8. | Case History | 510 | ||||
| 9. | Costs | 510 | ||||
| 10. | Example | 513 | ||||
| Nomenclature | 515 | |||||
| References | 515 | |||||
| Appendix | 518 | |||||
| 17 | Belt Filter Presses | |||||
| Nazih K. Shammas and Lawrence K. Wang | 519 | |||||
| 1. | Introduction | 519 | ||||
| 2. | Principles of Belt Filters | 520 | ||||
| 3. | Advantages and Disadvantages | 521 | ||||
| 4. | Application and Performance | 522 | ||||
| 5. | Design Criteria | 523 | ||||
| 6. | Design of High Pressure Zone | 525 | ||||
| 7. | Odor Control | 527 | ||||
| 8. | Operation and Maintenance | 528 | ||||
| 9. | Costs | 530 | ||||
| 10. | Design Examples | 532 | ||||
| 10.1 | Design Example 1 | 532 | ||||
| 10.2 | Design Example 2 | 533 | ||||
| 10.3 | Design Example 3 | 534 | ||||
| 10.4 | Design Example 4 | 535 | ||||
| Nomenclature | 536 | |||||
| References | 537 | |||||
| Appendix | 539 | |||||
| 18 | Pressure Filtration | |||||
| Nazih K. Shammas and Lawrence K. Wang | 541 | |||||
| 1. | Introduction | 541 | ||||
| 2. | Process Description | 543 | ||||
| 3. | Applicability | 546 | ||||
| 4. | Advances and Disadvantages | 546 | ||||
| 5. | Basis for System Design | 547 | ||||
| 6. | Evaluation of Design Parameters | 549 | ||||
| 6.1 | Types of Tests | 549 | ||||
| 6.2 | Test Procedures | 549 | ||||
| 7. | Design Procedures | 550 | ||||
| 8. | Support Equipment and Processes | 555 | ||||
| 8.1 | Biosolids Conditioning Process | 555 | ||||
| 8.2 | Feed Pump System | 557 | ||||
| 8.3 | Cloth Washing and Cleaning | 558 | ||||
| 8.4 | Dewatered Cake Breakers | 559 | ||||
| 9. | Operation, Maintenance, and Performance Characteristics | 559 | ||||
| 9.1 | Control of Machine Variables | 560 | ||||
| 9.2 | Control of Process Variables | 561 | ||||
| 9.3 | Control Considerations | 561 | ||||
| 10. | Survey of Filter Presses | 562 | ||||
| 11. | General Equipment Selection Criteria | 567 | ||||
| 12. | Costs | 567 | ||||
| 13. | Design Examples | 569 | ||||
| 13.1 | Design Example 1 | 569 | ||||
| 13.2 | Design Example 2 | 574 | ||||
| Nomenclature | 577 | |||||
| References | 578 | |||||
| Appendix | 581 | |||||
| 19 | Evaporation Processes | |||||
| Lawrence K. Wang, Nazih K. Shammas, Clint Williford, Wei-Yin Chen, and George P. Sakellaropoulos | 583 | |||||
| 1. | Introduction | 583 | ||||
| 1.1 | Drying and Evaporation Processes | 583 | ||||
| 1.2 | Natural Sludge Evaporation Lagoons and Evaporation Process Reactor | 584 | ||||
| 2. | Sludge Evaporation Lagoons (Sludge Drying Lagoons) | 585 | ||||
| 2.1 | Process Description | 585 | ||||
| 2.2 | Process Applications and Limitations | 586 | ||||
| 2.3 | Design Considerations | 587 | ||||
| 2.4 | Cost | 589 | ||||
| 3. | Evaporators | 590 | ||||
| 3.1 | Process Description | 590 | ||||
| 3.2 | Process Applications and Limitations | 593 | ||||
| 3.3 | Design Considerations | 593 | ||||
| 4. | Design Examples | 597 | ||||
| 4.1 | Example 1 | 597 | ||||
| 4.2 | Example 2 | 598 | ||||
| 4.3 | Example 3 | 599 | ||||
| 4.4 | Example 4 | 600 | ||||
| 4.5 | Example 5 | 601 | ||||
| 4.6 | Example 6 | 601 | ||||
| 4.7 | Example 7 | 601 | ||||
| 4.8 | Example 8 | 603 | ||||
| 4.9 | Example 9 | 604 | ||||
| 4.10 | Example 10 | 605 | ||||
| Nomenclature | 609 | |||||
| References | 610 | |||||
| Appendix | 612 | |||||
| 20 | High Temperature Thermal Processes | |||||
| Clint Williford, Wei-Yin Chen, Lawrence K. Wang, and Nazih K. Shammas | 613 | |||||
| 1. | Introduction | 613 | ||||
| 2. | Principles of High Temperature Operations - Combustion Factors | 614 | ||||
| 2.1 | Sludge Fuel Values | 614 | ||||
| 2.2 | Oxygen Requirements for Complete Combustion | 617 | ||||
| 2.3 | Factors Affecting the Heat Balance | 617 | ||||
| 2.4 | Example | 619 | ||||
| 3. | Technology Review | 620 | ||||
| 3.1 | Incineration of Sludge FBF | 620 | ||||
| 3.2 | Incineration of Sludge MHF | 624 | ||||
| 3.3 | Codisposal by Combustion | 627 | ||||
| 3.4 | SAC of Sludge | 629 | ||||
| 4. | Incineration Design Example | 632 | ||||
| 4.1 | Problem Statement | 632 | ||||
| 4.2 | Approximate Calculation Method | 633 | ||||
| 4.3 | Theoretical Calculation method | 638 | ||||
| 4.4 | Comparison of Approximate and Theoretical Calculation Methods | 641 | ||||
| 5. | Regulatory Matters | 642 | ||||
| Nomenclature | 642 | |||||
| References | 642 | |||||
| 21 | Biosolids Composting | |||||
| Nazih K. Shammas and Lawrence K. Wang | 645 | |||||
| 1. | Introduction | 645 | ||||
| 2. | Applicability and Environmental Impact | 647 | ||||
| 3. | Compost Quality | 649 | ||||
| 4. | Process Description | 651 | ||||
| 4.1 | Moisture | 651 | ||||
| 4.2 | Temperature | 653 | ||||
| 4.3 | pH | 653 | ||||
| 4.4 | Nutrient Concentration | 653 | ||||
| 4.5 | Oxygen Supply | 653 | ||||
| 5. | Design Criteria and Procedures | 654 | ||||
| 5.1 | Compost Processes With No External Bulking Agent | 656 | ||||
| 5.2 | Compost Processes Using External Bulking Agent | 658 | ||||
| 6. | Windrow Process | 659 | ||||
| 6.1 | Methodology and Design | 659 | ||||
| 6.2 | Energy Requirements | 662 | ||||
| 6.3 | Public Health and Environmental Impacts | 662 | ||||
| 7. | Aerated Static Pile Process | 664 | ||||
| 7.1 | Process Description | 664 | ||||
| 7.2 | Individual Aerated Piles | 665 | ||||
| 7.3 | Extended Aerated Piles | 666 | ||||
| 7.4 | Oxygen Supply | 666 | ||||
| 7.5 | Bulking Agents | 667 | ||||
| 7.6 | Energy Requirements | 667 | ||||
| 7.7 | Public Health and Environmental Impacts | 668 | ||||
| 8. | In-Vessel Composting System | 669 | ||||
| 8.1 | Process Description | 669 | ||||
| 8.2 | Advantages and Disadvantages | 673 | ||||
| 8.3 | Applicability | 673 | ||||
| 9. | Costs | 674 | ||||
| 10. | Design Examples | 675 | ||||
| 10.1 | Design Example 1 - Windrow Process | 675 | ||||
| 10.2 | Design Example 2 - Extended Aerated Pile System | 678 | ||||
| Nomenclature | 682 | |||||
| References | 683 | |||||
| Appendix | 687 | |||||
| 22 | Vermicomposting Process | |||||
| Lawrence K. Wang, Yung-Tse Hung, and Kathleen Hung Li | 689 | |||||
| 1. | Introduction | 689 | ||||
| 1.1 | Summary | 689 | ||||
| 1.2 | Process Description | 690 | ||||
| 2. | Technology Development | 690 | ||||
| 3. | Problems and Technology Breakthrough | 694 | ||||
| 3.1 | Introduction | 694 | ||||
| 3.2 | Problems | 694 | ||||
| 3.3 | Progress in Vermicomposting Outside the United States | 696 | ||||
| 4. | Pioneers, Current Status, and Resources | 697 | ||||
| 4.1 | Pioneers and Current Status | 697 | ||||
| 5. | Process Design Considerations | 698 | ||||
| 5.1 | Process Adoption and Advantages | 698 | ||||
| 5.2 | Process Operation and Troubleshooting | 699 | ||||
| 5.3 | Process Limitations | 700 | ||||
| 5.4 | Process Design Criteria | 700 | ||||
| 6. | Process Application Examples | 701 | ||||
| 7. | Future Development and Direction | 701 | ||||
| References | 701 | |||||
| 23 | Land Application of Biosolids | |||||
| Nazih K. Shammas and Lawrence K. Wang | 705 | |||||
| 1. | Introduction | 705 | ||||
| 2. | Recycling of Biosolids Through Land Application | 706 | ||||
| 3. | Description | 706 | ||||
| 4. | Advantages and Disadvantages | 708 | ||||
| 5. | Design Criteria | 709 | ||||
| 6. | Performance | 710 | ||||
| 7. | Cost of Recycling Through Land Application | 712 | ||||
| 8. | Biosolids Disposal on Land (Landfill) | 712 | ||||
| 9. | Biosolids Landfill Methods | 713 | ||||
| 9.1 | Biosolids-Only Trench Fill | 713 | ||||
| 9.2 | Biosolids-Ony Area Fill | 714 | ||||
| 9.3 | Co-Disposal With Refuse | 716 | ||||
| 9.4 | Landfilling of Screenings, Grit, and Ash | 717 | ||||
| 10. | Preliminary Planning | 717 | ||||
| 10.1 | Biosolids Characterization | 717 | ||||
| 10.2 | Selection of a Landfilling Method | 719 | ||||
| 10.3 | Site Selection | 719 | ||||
| 11. | Facility Design | 722 | ||||
| 11.1 | Regulations and Standards | 722 | ||||
| 11.2 | Site Characteristics | 722 | ||||
| 11.3 | Landfill Type and Design | 724 | ||||
| 11.4 | Ancillary Facilities | 724 | ||||
| 11.5 | Landfill Equipment | 728 | ||||
| 11.6 | Flexibility, Performance, and Environmental Impacts | 728 | ||||
| 12. | Operation and Maintenance | 728 | ||||
| 12.1 | Operations Plan | 731 | ||||
| 12.2 | Operating Schedule | 731 | ||||
| 12.3 | Equipment Selection and Maintenance | 731 | ||||
| 12.4 | Management and Reporting | 731 | ||||
| 12.5 | Safety | 733 | ||||
| 12.6 | Environmental Control | 733 | ||||
| 13. | Site Closure | 735 | ||||
| 13.1 | Ultimate Use | 735 | ||||
| 13.2 | Grading at Completion of Filling | 735 | ||||
| 13.3 | Landscaping | 735 | ||||
| 13.4 | Continued Leachate and Gas Control | 735 | ||||
| 14. | Costs of Biosolids Disposal on Land (Landfill) | 735 | ||||
| 14.1 | General | 735 | ||||
| 14.2 | Hauling of Biosolids | 736 | ||||
| 14.3 | Energy Requirements | 738 | ||||
| 14.4 | Costs | 738 | ||||
| 15. | Examples | 741 | ||||
| 15.1 | Example 1 Typical Biosolids Application Rate Scenario | 741 | ||||
| 15.2 | Example 2 Hauling of Biosolids | 741 | ||||
| Nomenclature | 742 | |||||
| References | 742 | |||||
| Appendix | 745 | |||||
| Appendix: Conversion Factors | ||||||
| Lawrence K. Wang | 747 | |||||
| Index | 811 | |||||
Preface
The past thirty years have seen the emergence of a growing desire worldwide that positive actions be taken to restore and protect the environment from the degrading effects of all forms of pollution - air, water, soil, and noise. Because pollution is a direct or indirect consequence of waste, the seemingly idealistic demand for "zero discharge" can be construed as an unrealistic demand for zero waste. However, as long as waste continues to exist, we can only attempt to abate the subsequent pollution by converting it to a less noxious form. Three major questions usually arise when a particular type of pollution has been identified: (1) How serious is the pollution? (2) Is the technology to abate it available? and (3) Do the costs of abatement justify the degree of abatement achieved? This book is one of the volumes of the Handbook of Environmental Engineering series. The principal intention of this series is to help readers formulate answers to the above three questions.
The traditional approach of applying tried-and-true solutions to specific pollution problems has been a major contributing factor to the success of environmental engineering, and has accounted in large measure for the establishment of a "methodology of pollution control." However, the realization of the ever-increasing complexity and interrelated nature of current environmental problems renders it imperative that intelligent planning of pollution abatement systems be undertaken. Prerequisite to such planning is an understanding of the performance, potential, and limitations of the various methods of pollution abatement available for environmental scientists and engineers. In this series of handbooks, we will review at a tutorial level a broad spectrum of engineering systems (processes, operations, and methods) currently being utilized, or of potential utility, for pollution abatement. We believe that the unified interdisciplinary approach presented in these handbooks is a logical step in the evolution of environmental engineering.
Treatment of the various engineering systems presented will show how an engineering formulation of the subject flows naturally from the fundamental principles and theories of chemistry, microbiology, physics, and mathematics. This emphasis on fundamental science recognizes that engineering practice has in recent years become more firmly based on scientific principles rather than on its earlier dependency on empirical accumulation of facts. It is not intended, though, to neglect empiricism where such data lead quickly to the most economic design; certain engineering systems are not readily amenable to fundamental scientific analysis, and in these instances we have resorted to less science in favor of more art and empiricism.
Because an environmental engineer must understand science within the context of application, we first present the development of the scientific basis of a particular subject, followed by exposition of the pertinent design concepts and operations, and detailed explanations of their applications to environmental quality control or remediation. Throughout the series, methods of practical design and calculation are illustrated by numerical examples. These examples clearly demonstrate how organized, analytical reasoning leads to the most direct and clear solutions. Wherever possible, pertinent cost data have been provided.
Our treatment of pollution-abatement engineering is offered in the belief that the trained engineer should more firmly understand fundamental principles, be more aware of the similarities and/or differences among many of the engineering systems, and exhibit greater flexibility and originality in the definition and innovative solution of environmental pollution problems. In short, the environmental engineer should by conviction and practice be more readily adaptable to change and progress.
Coverage of the unusually broad field of environmental engineering has demanded an expertise that could only be provided through multiple authorships. Each author (or group of authors) was permitted to employ, within reasonable limits, the customary personal style in organizing and presenting a particular subject area; consequently, it has been difficult to treat all subject material in a homogeneous manner. Moreover, owing to limitations of space, some of the authors' favored topics could not be treated in great detail, and many less important topics had to be merely mentioned or commented on briefly. All authors have provided an excellent list of references at the end of each chapter for the benefit of the interested readers. As each chapter is meant to be self-contained, some mild repetition among the various texts was unavoidable. In each case, all omissions or repetitions are the responsibility of the editors and not the individual authors. With the current trend toward metrication, the question of using a consistent system of units has been a problem. Wherever possible, the authors have used the British system (fps) along with the metric equivalent (mks, cgs, or SIU) or vice versa. Conversion Factors for Environmental Engineers are attached as an appendix in this handbook for the convenience of international readers. The editors sincerely hope that this duplicity of units' usage will prove to be useful rather than being disruptive to the readers.
The goals of the Handbook of Environmental Engineering series are: (1) to cover entire environmental fields, including air and noise pollution control, solid waste processing and resource recovery, physicochemical treatment processes, biological treatment processes, biosolids management, water resources, natural control processes, radioactive waste disposal, and thermal pollution control; and (2) to employ a multimedia approach to environmental pollution control since air, water, soil, and energy are all interrelated.
As can be seen from the above handbook coverage, no consideration is given to pollution by type of industry or to the abatement of specific pollutants. Rather, the organization of the handbook series has been based on the three basic forms in which pollutants and waste are manifested: gas, solid, and liquid. In addition, noise pollution control is included in the handbook series.
This particular book, Volume 6, Biosolids Treatment Processes, is a sister book to Volume 7, Biosolids Engineering and Management. Both biosolids books have been designed to serve as basic biosolids treatment textbooks as well as comprehensive reference books. We hope and expect they will prove of equal high value to advanced undergraduate and graduate students, to designers of wastewater, biosolids, and sludge treatment systems, and to scientists and researchers. The editors welcome comments from readers in all of these categories. It is our hope that both books will not only provide information on the physical, chemical and biological treatment technologies, but will also serve as a basis for advanced study or specialized investigation of the theory and practice of individual biosolids management systems.
This book, Volume 6, Biosolids Treatment Processes, covers the topics of biosolids characteristics and quantity, gravity thickening, flotation thickening, centrifugation, anaerobic digestion, aerobic digestion, lime stabilization, low temperature thermal processes, high temperature thermal processes, chemical conditioning, stabilization, elutriation, polymer conditioning, drying, belt filter, composting, vertical shaft digestion, flotation, biofiltration, pressurized ozonation, evaporation, pressure filtration, vacuum filtration, anaerobic lagoons, vermicomposting, irradiation, and land application.
The sister book, Volume 7, Biosolids Engineering and Management, covers additional topics on sludge and biosolids transport, pumping and storage, sludge conversion to biosolids, waste chlorination for stabilization regulatory requirements, cost estimation, beneficial utilization, agricultural land application, biosolids landfill engineering, ocean disposal technology assessment, combustion and incineration, and process selection for biosolids management systems.
The editors are pleased to acknowledge the encouragement and support received from their colleagues and the publisher during the conceptual stages of this endeavor. We wish to thank the contributing authors for their time and effort, and for having patiently borne our reviews and numerous queries and comments. We are very grateful to our respective families for their patience and understanding during some rather trying times.
Lawrence K. Wang, Lenox, MA
Nazih K. Shammas, Lenox, MA
Yung-Tse Hung, Cleveland, OH
HANDBOOK OF ENVIRONMENTAL ENGINEERING VOLUME 6
Biosolids Treatment Processes
Edited by
Lawrence K. Wang, PhD, PE, DEE
Zorex Corporation, Newtonville, NY
Lenox Institute of Water Technology, Lenox, MA
Krofta Engineering Corporation, Lenox, MA
Nazih K. Shammas, PhD
Lenox Institute of Water Technology, Lenox, MA
Krofta Engineering Corporation, Lenox, MA
Yung-Tse Hung, PhD, PE, DEE
Department of Civil and Environmental Engineering
Cleveland State University, Cleveland, OH
The past 30 years have seen the emergence of a growing desire worldwide to take positive actions to restore and protect the environment from the degrading effects of all forms of pollution: air, noise, solid waste, and water. The Handbook of Environmental Engineering series guides readers to answer the fundamental questions facing pollution in the modern era - How serious is pollution? Is the technology needed to abate it not only available, but feasible? Among the topics included in this, the sixth volume, are: biosolids properties, thickening, stabilization, disinfection, conditioning, dewatering, high temperature processes, drying, composting, utilization and disposal to land.
Cutting-edge and highly practical, the Handbook of Environmental Engineering, Volume Six, Biosolids Treatment Processes offers educators, students, and engineers a strong grounding in the principles of environmental engineering, as well as providing effective methods for developing optimal abatement technologies at costs that are fully justified by the degree of abatement achieved. With an emphasis on using the best available technologies, the authors of these volumes present the necessary engineering protocols derived from the fundamental principles of chemistry, physics, and mathematics, making these volumes essential references for environmental pollution researchers.
Contents
Characteristics and Quantity of Biosolids. Gravity Thickening. Flotation Thickening. Centrifugation Clarification and Thickening. Anaerobic Digestion. Aerobic Digestion. Lime Stabilization. Pressurized Ozonation. LowTemperature Thermal Treatment Processes. Irradiation and Solid Substances Disinfection. Inorganic Chemical Conditioning and Stabilization. Elutriation and Polymer Conditioning. Drying Beds. Animal Wastes Treatment Using Anaerobic Lagoons. Vertical Shaft Digestion, Flotation and Biofiltration. Vacuum Filtration. Belt Filter Presses. Pressure Filtration. Evaporation Processes. High Temperature Thermal Processes. Biosolids Composting. Vermicomposting Process. Land Application of Biosolids. Appendix: Conversion Factors. Index.
Handbook of Environmental Engineering
VOLUME 6: BIOSOLIDS TREATMENT PROCESSES
ISBN: 978-1-58829-396-1
E-ISBN: 978-1-59259-996-7
humanapress.com
Index
AAcid
- forming bacteria, 137
- phase, 137
Activated sludge, 10-22
- production, 10-13
Adsorber, 287
Aerated static pile bulking agents, 667
- energy requirements, 667-668
- environmental impact, 668-669
- oxygen supply, 666-667
- process, 664-670
- - description, 664
Aerobic digestion, 177-205, 456-463
- advantages, 178
- air requirement, 195
- autothermal thermophilic, 179-180
- - using oxygen, 181
- capital costs, 189-191
- continuous operation, 179
- design, 186-189
- - considerations, 181-185
- - - dewatering, 194-195
- - - mixing, 194
- - - oxygen requirements, 183-184
- - - pH reduction, 194
- - - solids reduction, 182-183
- - - temperature, 181-182
- - input-output data, 186-189
- - parameters, 186-188
- - performance
- - - supernatant quality, 185-186
- - - volatile solids reduction, 185
- - - volatile solids loading, 194
- - design procedure, 186-189
- digester volume, 193-194, 196-197
- disadvantages, 178-179
- microbiology, 178
- O&M costs, 190-191
- oxygen requirement, 194-195, 196
- performance, 185-186
- power requirement, 197
- process
- - description, 178-179
- - variations, 179-181
- semibatch operation, 179
- sludge
- - age, 196
- - quantity, 193
- - wasting schedule, 194
- solids retention time, 194
- volatile solids reduction, 196
Agitated in-vessel composting bioreactor, 671
Air
- and oxygen requirements, complete combustion, 618
- compression, 265
- drying, 265- filtration, 265
- preparation, ozone, 265
- saturation, flotation, 86
- to-solids ratio, 81, 89, 90, 92, 93
Alkaline stabilization, 207
- advantages and disadvantages, 212
- biosolids
- - chemical characteristics, 220
- - environmental impacts, 213
- - deodorization, 217
- - equipment, 216
- - facility for biosolids, design factors, 216
- - process performance, 217
- chemical compounds in biosolids, 221, 222
- process design, 223
- - lime handling facilities, 223
Anaerobic
- biological reactions, 136
- contact
- - column schematic, 150
- - process study procedures, 146
- - schematic, 140
- decomposition, 135
- digester
- - capital and operating costs, 162
- - cost estimate, 162, 163
- - covers, 150
- - design examples, 163
- - - using modified anaerobic contact process, 167
- - - using standards design, 163
- - - performance criteria, 162
- - reactor configuration, 139
- - external heat exchanger, 157
- - gas
- - - collection, storage, and distribution, 158
- - - piping schematic, 159
- - - utilization, 159
- - heating system, 154
- - heat losses, 156
- - maintenance of reactor stability, 161
- - mixing devices, 151
- - sludge and supernatant withdrawal, 161
- - sludge pumping and piping considerations, 160
- - system equipment and appurtenances, 150
- - tank construction and system components, 149
- - turbine-type mixing system, 155
- digestion, 135, 457, 484, 487
- - effect of solid detention time, 142
- - effect of temperature, 142
- - gas production and utilization, 142
- - management, 160
- - management, control of sludge feed, 160
- - nutrient requirements, 142
- - organic loading
- - - parameters, 140
- - - rate, 141
- - reactor configurations, 138
- - - anaerobic contact process with sludge recycle, 138
- - - anaerobic filter, 138
- - - single-stage, unmixed, 138
- - - two-stage, mixed primary, 138
- - solid waste, 135
- - time and temperature relationships, 141
- - wastewater sludges, 135
- lagoons, 431, 432
- - applications, 432
- - application examples, 443
- - construction cost, 440
- - design criteria, 437
- - design
- - - examples, 443
- - - data gathering and compilation, 437
- - energy
- - - consumption, 440
- - - costs, 440
- - limitations, 432
- - minimum top width, embankments, 439
- - minimum treatment volume, 433
- - operation and maintenance cost, 440
- - process
- - - design, 433
- - - performance, 432
- - - reliability, 432
- - sludge volume, 436
- - volumes and depth requirement, 434
- - waste volume for treatment period, 434
- - volume requirement, 436
- - with recycle system, 439
- process, 136
- - biochemistry, 137
- - metabolic pathways, 139
- - microbiology, 137
- - recent development, 168
- - performance data 171
- reactor design and sizing, 146
- treatability studies, design practice, 144
- treatment process, 136
- - advantages, 136
- trickling filter, 140
Ancillary facilities, landfill, 724
Animal wastes
- anaerobic lagoons, 431
- treatment, 431
Annual evaporation data, 600
Anoxic gas flotation, AGF, 492
Ash, 357
ATAD, autothermal thermophilic aerobic digester, 452, 456-463, 488- air, 191-193, 452, 456, 460
- oxygen, 191-193, 452, 456, 462-463
Attached-suspended growth biosolids, 26-27
Average evaporation data in US, 438
BBacteria, 334-335
Basket centrifuge, 103-104
- achievable solids concentration, 103
- costs, 109-110
- - construction, 113
- - O&M, 114
- cycle time, 103
- energy requirements, 109-110- feed rate, 103
- performance, 109-110, 118
Belt press, 255-258, 466
Belt filter presses, 519-539
- advantages, 521-522
- applications, 522
- cake thickness, 534
- capital cost, 530
- costs, 530-532
- design criteria, 523-527
- - pressures, 526-527
- disadvantages, 522
- energy requirements, 533-534
- O&M, 528-530
- - belt
- - - rate travel, 530
- - - tracking, 529
- - biosolids conditioning, 529
- - compression, 530
- - costs, 530-532
- - inspection, 529
- - loading rate, 530
- - sampling and analysis, 529
- - solids, 529
- - spray adjustment, 529
- odor control, 527-528
- performance, 522-523
- pressing capacity, 533
- pressures, 534
- principles, 520-21
- weight of water in cake, 534
Biofiltration, 451, 453, 464, 466-470, 481
- applications, 468
- costs, 469
- design considerations, 468
- process description, 467
Biological
- biosolids, 10-27
- - characteristics, 10- flotation, 72
Biosolids
- and site conditions, 720
- anaerobic
- - digestion, 135
- - anaerobic lagoon, 432
- bacteria, 219
- centrifugation, 101-134, 466
- characteristics and quantity, 1-44
- characterization, 28-35, 717
- chlorine stabilization, 376-383
- class A, 707
- class B, 707
- codisposal with refuse, 716
- combustion, 614-618
- composting, 645-687
- - applicability, 647-649
- - calculation of composting area requirements, 681-682
- - calculation of bulking agent to biosolids ratio, 679
- - calculation of the ratio of new to recycled bulking agent, 679-681
- - costs, 674-675
- - - capital, 674-675
- - design criteria, 654-659
- - environmental impact, 647-649
- - O&M, 675
- - process description, 651-654
- compressibility, 33-34
- conditioning cost, 364-368
- - capital, 364-365
- - electricity means, 375
- - O&M cost, 365-368
- dewaterability, 29-31
- dewatering processes, 465
- digestion and stabilization, 454
- disposal on land (landfill), 712
- elutriation, 389
- evaporation, 583- fixed solids, 34
- flotation, 71, 451
- heavy metals, 34-35
- high temperature thermal processes, 613
- incineration, 620-627
- land application program, elements, 712
- landfill methods, 713
- - area fill layer, 715
- - area fill mound, 715
- - biosolis-only area fill, 714
- - biosolids-only trench fill, 713
- - dike containment, 715
- - narrow trenches, 713
- - wide trenches, 714- lime mixing tank
- - design, 228
- - mixing, 230
- - sizing, 229
- low temperature thermal processes, 299
- management, 4- oxyozosynthesis, 244
- pH, 34
- polymer conditioning, 389
- pressurized ozonation, 243
- production, 2, 737
- property, exceptional quality, 707
- septicity, 34
- sludge drying beds, 403
- slurries, mechanical mixer specifications, 231
- specific gravity, 28-29
- specific resistance, 33
- stabilization, 375-376
- - lime dose requirement, 214, 215
- storage with lime addition, pH change, 216
- temperature, 34
- thickening, 30-31, 71
- trace elements, 34-45
- vermicomposting, 689
- vertical shaft digestion, 451
- volatile solids, 34
- wasting methods, 20
- bridging model, destabilization of colloids by polymers, 397
Buchner funnel test, 362-364
CCapillary suction time (CST), 364
- testing, 549-550
Capital cost, codisposal by combustion, starved air combustion (SAC), 629
Carver-Greenfield dehydration system, 591
Cationic polyelectrolyte in solution, configuration, 396
Cement kiln dust, 357
Centrifugation, 101-134, 466
- advantages, 124
- clarification and thickening, 101-134
- cannery waste sludge, 122
- coal and refuse, 114-121
- disadvantages, 124
- electroplating waste, 112-114
- metallurgical refinery sludge, 121-122
- paper sludges, 110-112
- potato wastes, 122
- principles, 102
- pulp sludges, 110-112
Centrifuges
- construction material, 124
- design, 122-126
- - applications, 128
- - criteria, 125
- - procedure, 125-126
- effects of parameters, 125
- manufacturers, 123-124
- operation and maintenance, 126-128
- performance, 109-122
- selection, 122
- types, 103
Chemical biosolids, 27-28
- conditioning of, 354
Chemisorbed water, 102-103
Chlorine, 272
- stabilization, 376-383
- - advantages, 379-380
- - characteristics of stabilized biosolids, 380-381
- - chlorine requirements, 379-380
- - cost, 381-383
- - disadvantages, 380
- - process description, 376-378
- - subnatant quality, 381
- - supernatant quality, 381
Clarification, centrifugation, 101-134
Class A biosolids, 209
Class B biosolids, 209
Classical pollutant removal- flotation, 256
- ozonation, 250, 289
Closed-loop ozonation, 288
Coal, 357
Codisposal by combustion, 627
- applications, 628
- design basis for costs, 629
- design parameters, 628
- energy requirements, 629
- environmental impact, 629
- performance, 628
- reliability, 628
- starved air combustion (SAC), 628
- - operating cost, 630
Codisposal, biosolids/refuse mixture, 716
Codisposal, biosolids/soil mixture, 716
Coil spring-belt type vacuum filter, 500
Colloidally bound water, 102-103
Combustion, 614-18
- calculations, molal basis, 639
- chemical reactions, 616
Comparison, approximate and theoretical calculation, 641
Complete mix digester design, mean cell residence times, 148
Completely mixed biological waste treatment process, steady-state relationships, 148
Composition of primary biosolids, 9-10
Compost, 338, 464, 650-653
- class A, 650
- class B, 650
- Exception Quality (EQ), 650
- metal concentration, 650
- processes
- - with external bulking agent, 658-659
- - without external bulking agent, 656-658
- quality, 649-651
- temperature, 650
Composted sludge, gamma irradiation, 345
Composting, 338, 646
- moisture, 651-653
- nutrient concentration, 653
- oxygen supply, 653
- pH, 653
- temperature, 653
Concurrent elutriation in multiple tanks, 393
Conditioning
- and stabilization, 353-388
- chemical, 359-364
- dosage, 357-358
Conduction drying, 306
Continued leachate and gas control, landfill, 735
Continuous
- flow system, 695
- slaking, 228
Convection drying, 305
Conventional digester, 138
Cost
- biosolids disposal on land (landfill), 735
- flotation, 86
- hauling of biosolids, 738
- heat
- - conditioning, 303
- - drying, 308
- of recycling, land application, 712
- supplemental heat, lime addition and electricity, 232
- sludge drying bed, 420
- VSD, 486, 488
Countercurrent elutriation, 390
Cryogenic air separation, 285-286
Cryophilic aerobic digestion, 192
CT, concentration-time, 276
Cyanide removal, ozonation, 291
DDAF (see also Dissolved air flotation)
- concrete or steel construction, 76
- dissolved air flotation, 71, 251-255, 453
- hydraulic loading, 79, 82
- pollutants removal, 256
- rectangular or circular shape, 76, 78
- solids loading, 80
- thickener, 71-99, 463
- - design criteria, 73
- - no recycle, 89, 91
- - process description, 74
- - process design, 88
- - with recycle, 90, 93
- - performance, 85
Decay coefficient, 14, 16, 17
Deep-shaft bioreactor (VSB), 452
Denitrification biosolids, 27
Design criteria
- for area fill layer, 716
- for area fill mound, 716
- for diked containment landfill, 716
- narrow trench landfill, 714
- wide trench landfill, 714
Design
- parameters, hauling of biosolids, 736
- procedure, hauling of biosolids, 736
Diffuser contactor for water and wastewater treatment, 267-268
Digester
- gas holder cover, 152
- heat transfer coefficients, 156
Digestion, 451-489
Dilution-to-threshold, D/T, 481
Direct
- drying, 305
- indirect rotary dryer, 320-321
Disinfection
- chemical, 336
- chlorine, 337
- electron irradiation, 339
- gamma irradiation, 343-349
- heat drying, 327
- high temperature thermal process, 338
- lime, 337
- long-term storage, 336
- low temperature thermal process, 337
- ozonation, 251, 276
- ozone, 274-276, 337
- quaternary ammonium compounds, 337
- solid substances, 336
Disk centrifuge, 107-108
- advantages, 108
- disadvantages, 108
- performance, 109
Dispersed air flotation, 71
Dissolved air flotation (DAF), 71, 251-255, 453
- double cell, 253
- single cell, 252
Dissolved gas flotation (DGF), 247-252
DO, dissolved oxygen, 15
Draft tube-type mixer, 154
Dried sludge, gamma irradiation, 345
Dry
- feeders, 227
- powder cationic polyelectrolytes, 395
- solids heating values, effect on autogenous combustion, 621
- solids heating values, effect on supplemental fuel consumption, 622
Drying
- beds, 403-430, 466
- lagoons, 585-590
- conduction, 306
- convection, 305
Dual digestion, 484, 485
EE. foetida, 691
Earthworm
- conversion process, process design- - considerations, 698
- - criteria, 700
- - limitations, 700
- - operation, 699
- - troubleshooting, 699
- process diagram, 691
Efficiencies, biosolids de watering processes, 737
Electroflotation, 72
Electron beam- facility, 340
- scanner, 341
Electron irradiation, 339-343
- design considerations, 341
- performance, 342
- process description, 340
Elutriation, 373, 36, 389
- chemical conditioning, soluble ionic organic polymers (polyelectrolytes), 394
- chemical conditioning, soluble nonionic organic polymers, 394
- design examples, 399
- elutriate disposal considerations, 391
- process
- - benefit, 392
- - design
- - - considerations, 390
- - - new technology considerations, 391
- - - procedures, 392
- reactor design considerations, 390
Energy requirements, hauling of bio-solids, 738
Environmental
- control, landfill, 733, 734
- impact, DAF, 87
- problems, landfill, 734
Equipment
- landfill, 732
- performance characteristics, landfill, 729, 730
- selection and maintenance, landfill, 731
Eudrilus eugeniae, 691
Evaporation
- data, USA, 600
- lagoons, 584-590
- process reactor, 584, 602
Evaporative efficiency, 313
Evaporator, 590-604
- applications and limitations, 592
- design considerations, 593
- heat transfer coefficients, 594
- multiple-effect, 596, 598
- process description, 590
- single-effect, 595
- solar, 603
- steam, 602
- triple-effect, 592
- vertical short-tube, 591
Examples, land application, 741
Excess air
- effect on supplemental fuel requirement, 618
- temperature, effect on supplemental fuel requirement, 618
Extended aerated piles, 666
FF/M ratio, 13, 17, 19
Facility design, landfill, 722
Factors affecting
- biosolids conditioning, 354-356
- solids removal, 7-9
- the heat balance, 617
- that influence the production of WAS, 13-16
FBF, fluidized furnace, 620-623
Feed
- composition, 15
- pattern, 16
- pump, 54
Ferric chloride, 356-357
Fiber-cloth-belt type vacuum filter, 500
Film layer purifying chamber contactor for water, 266, 267
Filter
- leaf testing, 360-362
- media, 505-506
- process control cake drying, 508
- - chemical conditioning, 508
- - efficiency, 508- - filter cake quality
- - - heat treated biosolids, 508
- - inspection, 509
- - odor, 509
- - optimum operation, 508
- - production, 508-09
- - sampling and analysis, 509
- - tank agitation, 508
- - yield, 508
Filtration dewatering- basic theory, 495
- filter aids, 495-496
- pressure drop, 495
- system, 495-497
Fixed digester cover, 151
Fixed-volume recessed plate filter press, 542, 545
Flash dryer system, 315
Flash drying process, 316
Flexibility, performance, and environmental impacts, landfill, 728
Float concentration, 82
Floating digester cover, 152
Flotation, 71-99, 251-255, 451, 462
- cost, 86
- heavy metal removal, 256
- organic chemical removal, 256
- thickener, 462, 487fluidized bed furnace, FBF, 620-623
- applications, 623
- design basis for cost, 624
- design criteria, 623
- energy requirements, 624
- environmental impact, 624
- operation data, 624
- performance, 623
Food pasteurization, 337
Free water, 102-103
Freeze-thaw, 373-374
Fuel energy consumption rates, construction equipment, 738
Fungi, 336
Furnace combustion, comparison, approximate and theoretical calculation, 641
GGamma irradiation, 343-349
- design considerations, 346
- dried or composted sludge, 345- facility, 344
- labor requirements, 347-348
- operational considerations, 348
- power requirement, 345
Gas-phase biofiltration, 451, 453, 464, 466-470, 481
GLUMRB Standards, 146
Grading at completion of filling, landfill, 735
Gravity thickeners, 47-55
- advantages, 47, 48
- capital cost, 55
- compression and storage zone, 53
- cost, 55-56
- design, 56-61
- - considerations, 49
- - input data, 57, 58
- - output data, 61
- - parameters, 58
- - procedure, 59- floor slope, 54
- free board, 53
- hydraulic loading, 50
- maintenance materials cost, 56, 57
- minimum surface area, 49-51
- O&M cost, 55-57- overflow rates, 52
- polymer addition, 54
- power consumption, 56
- settling zone, 53
HHauling of biosolids, 736
- example, 741
Heating values, sludges, 616
High rate (mixed) digester, 141
High temperature- operations
- - principles, 614
- - - combustion factors, 614
- - - sludge fuel values, 614
- processes, 613
- - basic elements, 615
- - example, 619
- - technology review, 620
- thermal processes, 613
- - advantages, 614
High-rate digestion- systems, 138
- VS reduction, 143
Hydrogen sulfide/sulfide equilibrium, pH- effect, 218
IIncineration
- design example, 632
- of sludge FBF, 621
Inorganic polymer conditioning process, thickening and dewatering, 399
Input data, hauling of biosolids, 736
LLand application
- advantages, 708
- of biosolids, 705
- - description, 706
- - introduction, 705
- - maximum metal concentrations, 708
- - preliminary planning, 717
- design criteria, 709
- disadvantages, 708
- performance, 710
- site suitability, 709
Landfill
- burial, lime stabilized biosolids, 211
- design criteria, 725
- equipment, 728
- method, selection, 719
- type and design, 724
Landfilling of screenings, grit, and ash, 717
Landscaping, landfill, 735
Leachate quality from biosolids only
landfill, 727
Lime
- addition, biosolids, dewatering and settling characteristics, 219
- bulk density, 227
- characteristics, 223, 224
- delivery and storage, 225- feeding, 227
- - only and supplemental heating pasteurization, 234
- - capital and operating costs, 235
- - cost comparison, 235
- reaction
- - hydrated lime, 225
- - quick lime, 225
- stabilization, 207
- - current status and regulations, 208
- - design, 237
- - - component sizing, 237
- - - criteria, 213
- - - example, 235
- - - loading, 235, 236
- - - objective, 213- - full-scale lime stabilization facility, 208
- - history, 208
- - of biosolids, applicability, 211
- - operation, flow diagram, 210
- - pathogen reduction, 218
- - process description, 208
- - systems
- - - capital and operating costs, 232
- - - cost and energy usage, 232
- - - theory, 212
- storage and feed equipment, 226
Liquid
- cationic polyelectrolytes, 396
- sludge vermistabilization (LSVS) process, 692
LSVS reactors, 692
MManagement and reporting, landfill, 731
Maximum allowable pollutant concentrations, biosolids, landfill, 723
Mesophilic digestion, 141
Methane
- Fermentation Phase, 138- formation
- - bacteria, 137
- - step, 138
- production equation, 144
Minimum anaerobic digester capacities, 146
Multiple
- elutriation, 390
- - in a single tank, 392
- - hearth furnace- - - applications, 625
- - design basis for costs, 627
- - design criteria, 626
- - energy requirements, 626
- - environmental impact, 626
- - operations data, 627
- - performance, 626
OObligate anaerobes, 137
Operating schedule, landfill, 731
Operation and maintenance- biosolids landfill, 728
- costs
- - area landfill, 740
- - narrow and wide trench landfill, 739
Operations plan, landfill, 731
Organic wastes, nature, 136
Output data, hauling of biosolids, 737
Oxygen requirements, complete combustion, 617
PPart 503 Rule, 209, 707
PFRP treatment, 231
Pilot digester- schematic, 145
- study procedures, 145
Polyacrylamide molecule, 395
Polyelectrolyte
- additions for various sludges, 399
- conditioning process- - dewatering, 398
- - sludge thickening, 396
- determination, 399
- process control, 399
Polymer conditioning, 389
Process to Further Reduce Pathogens (PFRP) Requirements, 694
Progress in vermicomposting, outside US 696
PSRP treatment, 230
RRaw sludge VS reduction, 143
Recycling of biosolids, land application, 706
Reduction in volatile matter by digestion, 141
Regulations and standards, landfill, 722
SSAC, approximate combustion calculation, supplemental fuel requirements, 637
Safety, landfill, 733
Saprophytic bacteria, 137
Sick digesters, 137
Site and equipment costs- area landfill, 740
- narrow and wide trench landfill, 739
Site closure, landfill, 735
Site selection methodology, landfill, 721
Site selection, landfilling method, 719
Sludge
- heating system schematic, 155
- heating value, experimental methods, 616
- incineration
- - fluidized bed furnace, 623
- - multiple hearth furnace (MHF), 624, 625
- - regulatory matters, 642
- moisture
- - effect on autogenous combustion, 621
- - effect on supplemental fuel consumption, 622
- washing (elutriation), 390
Standard rate (unmixed) digester, 141
starved air combustion (SAC)- applications and limitations, 631
- approximate calculation method, 633
- capital cost, 633
- design basis for costs, 632
- design criteria, 632
- energy requirements, 632
- operating cost, 633
- performance, 631
- sludge, 629, 630
- theoretical calculation method, 638
Suitability of biosolids for landfill, 718
TThermophilic digestion, 141
TP AD process, performance parameter, 173
Two-stage anaerobic process, 137
Typical biosolids application
- rate scenario, example, 741
- scenarios, 711
Typical digester section, 149
UUltimate use, landfill, 735
US EPA 40 CFR Part 503, 209, 707, 722
VVermicomposting process, 689
- future development and direction, 701
- problems, 694
- process
- - application examples, 701
- - description, 690
- technology
- - breakthrough, 694
- - development, 690
Vermiconversion System, 695
Vermistabilization process- biosolids, 691
- current status, 697
- pioneers, 697
- resources, 697
Volatile solid loading factors, 147
- hydraulic detention time effect, 147
- sludge concentration effect, 147
WWaste storage ponds, 441
- cross-section, 442
- layout, 442
- process description, 441
- process design, 441
Wastewater and sludge treatment, process selection, flow sheet, 391
Contributors
DONALD B. AULENBACH, PhD Professor, Lenox Institute of Water Technology, Lenox, MA, and Rensselaer Polytchic Institute, Troy, NY
SHOOU-YUH CHANG, PhD, PE Professor, Department of Civil and Environmental Engineering, North Carolina A&T State University, Greensboro, NC
SATYA P. CHAUHAN, PhD Senior Program Manager, Battelle Columbus Laboratory, Columbus, OH
J. PAUL CHEN, PhD Assistant Professor, Department of Chemical and Biomolecular Engineering, National University of Singapore, Singapore
WEI-YIN CHEN, PhD Assistant Professor, Department of Chemical Engineering, University of Mississippi, University, MS
JFFREY GUILD, BS, MS Regional Manager, NORAM Engineering and Constructors, Ltd., Vancouver, BC, Canada
YUNG-TSE HUNG, PhD, PE, DEE Professor, Department of Civil and Environmental Engineering, Cleveland State University, Cleveland, OH
KATHLEEN HUNG LI, BS, MS Senior Technical Writer, NEC Unified Solutions, Irving, TX
YAN LI, PE, MS Environmental Engineer, Office of Waste Management, Department of Environmental Management, State of Rhode Island, Providence, RI
DAVID A. LONG, PhD Professor, Department of Civil Engineering, Pennslyvania State University, University Park, PA
H. S. MURALIDHARA, PhD Senior Research Scientist, Battele Columbus Laboratory, Columbus, OH
DAVID POLLOCK, BS Regional Manager, NORAM Engineering and Constructors, Ltd., Vancouver, BC, Canada
GEORGE P. SAKELLAROPOULOS, PhD Professor, Department of Chemical Engineering, University of Thessaloniki, Thessaloniki, Greece
WILLIAM A. SELKE, PhD Professor, Lenox Institute of Water Technology, Lenox, MA and Advisor, Krofta Engineering Corporation, Lenox, MA
NAZIH K. SHAMAS, PhD Professor and Environmental Engineering Consultant, Ex-Dean and Director, Lenox Institute of Water Technology, Lenox, MA, Krofta Engineering Corporation, Lenox, MA
JERRY R. TARICSKA, PhD, PE, DEE Senior Environmental Engineer/Associate, Hole Montes, Inc., Naples, EL
LAWRENCE K. WANG, PhD, PE, DEE Dean & Director (Retired), Lenox Institute of Water Technology, Lenox, MA; Assistant to the President (Retired), Krofta Engineering Corporation, Lenox, MA; Vice President (Retired), Zorex Corporation, Newtonville, NY
CLINT WILLIFORD, PhD Associate Professor, Department of Chemical Engineering, University of Mississippi, University, MS
ROBERT C. ZIEGLER, PhD Section Head (Retired), Environmental Systems Section, Arvin/Calspan Advanced Technology Center, Buffalo, NY
SHUAI-WEN ZOU, MEng Research Fellow, Department of Chemical and Biomolecular Engineering, National University of Singapore, Singapore
From the reviews: "This tome comprises 23 chapters of unequal length written by an ensemble of 20 authors ... . This book will be extremely useful to advanced undergraduate and graduate students - and I should also add to their teachers, preceptors and mentors -of civil and environmental engineering, to designers of wastewater treatment, biosolids and sludge treatment systems, and to scientists and researchers dealing with biosolids management operations." (J. G. LLaurado, Management of Environmental Quality, Vol. 19 (3), 2008)