BOOK
Innovative Wastewater Treatment & Resource Recovery Technologies: Impacts on Energy, Economy and Environment
Juan M. Lema | Sonia Suarez Martinez
(2017)
Additional Information
Book Details
Abstract
This book introduces the 3R concept applied to wastewater treatment and resource recovery under a double perspective. Firstly, it deals with innovative technologies leading to: Reducing energy requirements, space and impacts; Reusing water and sludge of sufficient quality; and Recovering resources such as energy, nutrients, metals and chemicals, including biopolymers. Besides targeting effective C,N&P removal, other issues such as organic micropollutants, gases and odours emissions are considered. Most of the technologies analysed have been tested at pilot- or at full-scale. Tools and methods for their Economic, Environmental, Legal and Social impact assessment are described.
The 3R concept is also applied to Innovative Processes design, considering different levels of innovation: Retrofitting, where novel units are included in more conventional processes; Re-Thinking, which implies a substantial flowsheet modification; and Re-Imagining, with completely new conceptions. Tools are presented for Modelling, Optimising and Selecting the most suitable plant layout for each particular scenario from a holistic technical, economic and environmental point of view.
Table of Contents
Section Title | Page | Action | Price |
---|---|---|---|
Cover | Cover | ||
Contents | v | ||
List of contributors | xix | ||
About the editors | xxix | ||
Preface | xxxi | ||
Part 1: Reducing Requirements and Impacts | 1 | ||
Part 1a: Reducing Energy Requirements | 1 | ||
Chapter 1: Nutrient removal | 3 | ||
1.1 INTRODUCTION | 3 | ||
1.1.1 Nutrient management regulation and implications on energy consumptions | 3 | ||
1.1.2 Biological Nutrients Removal processes: microbial and energy overview | 5 | ||
1.2 REDUCING ENERGY FOOTPRINT NOW, BY RETROFITTING | 8 | ||
1.2.1 Sidestream technologies/systems | 8 | ||
1.2.1.1 ELAN system: Pilot study and full scale retrofitting | 8 | ||
1.2.1.2 Attached growth biofilm (RBC-MBBR) pilot study and full scale retrofitting | 10 | ||
1.2.1.3 Short-Cut Enhanced Nutrient Abatement (S.C.E.N.A): pilot study and full scale retrofitting | 12 | ||
1.2.2 Mainstream technologies/systems | 15 | ||
1.2.2.1 Innovative (anoxic) BNR (BioP) including control automation | 15 | ||
1.2.2.2 Ion exchange for P recovery: pilot study and full scale retrofitting | 17 | ||
1.2.2.3 Via-nitrite mainstream biological nitrogen removal | 18 | ||
1.3 REDUCING ENERGY FOOTPRINT TOMORROW BY RE-THINKING | 19 | ||
1.3.1 Mainstream systems | 19 | ||
1.3.1.1 Systems with AnAmmOx for mainstream application: pilot scale results and full scale perspective | 19 | ||
1.3.1.2 AnoxAn: A novel anaerobic-anoxic reactor for biological nutrient removal | 22 | ||
1.3.1.3 Domestic wastewater treatment with purple phototrophic bacteria | 26 | ||
1.4 CONCLUDING REMARKS AND SUSTAINABILITY INDICATORS | 28 | ||
1.5 REFERENCES | 33 | ||
Chapter 2: Anaerobic treatment of municipal wastewater | 40 | ||
2.1 INTRODUCTION | 40 | ||
2.1.1 Energy nexus: Is anaerobic treatment a feasible way for municipal wastewater? | 41 | ||
2.2 ANAEROBIC REACTOR TYPES FOR MUNICIPAL WASTEWATER TREATMENT | 42 | ||
2.2.1 Anaerobic membrane bioreactor (AnMBR) | 42 | ||
2.2.2 Upflow anaerobic sludge blanket Reactor (UASB) | 45 | ||
2.2.3 Expanded granular sludge bed reactor (EGSB) | 46 | ||
2.2.4 Anaerobic sequencing batch reactor (ASBR) | 46 | ||
2.2.5 Anaerobic baffled reactor (ABR) | 47 | ||
2.2.6 Full scale applications | 47 | ||
2.2.7 Pilot scale applications | 48 | ||
2.2.8 Different lab-scale options – immobilization | 51 | ||
2.3 MODELING OF ANAEROBIC TREATMENT SYSTEMS | 52 | ||
2.3.1 Review of models | 52 | ||
2.3.2 Model selection for a given application | 53 | ||
2.4 PROBLEMS AND FUTURE PERSPECTIVES | 54 | ||
2.4.1 Problems | 54 | ||
2.4.2 Suggestions | 55 | ||
2.4.2.1 Source separation and anaerobic treatment of black water stream | 55 | ||
2.4.2.2 A hybrid system: algae combined with anaerobic digester | 56 | ||
2.5 FUTURE ASPECTS | 56 | ||
2.6 CONCLUSIONS | 57 | ||
2.7 REFERENCES | 57 | ||
Chapter 3: Resource recovery from source separated domestic wastewater; energy, water, nutrients and organics | 61 | ||
3.1 INTRODUCTION | 61 | ||
3.2 RESOURCES AND POLLUTANTS IN DOMESTIC WASTEWATER | 61 | ||
3.3 ANAEROBIC TREATMENT CORE TECHNOLOGY IN ‘NEW SANITATION’ | 62 | ||
3.3.1 Organic sludge and heavy metals | 62 | ||
3.3.2 Recovery of phosphorus during or after UASB treatment? | 63 | ||
3.3.3 Removal or recovery of nitrogen? | 63 | ||
3.4 REMOVAL OF MICROPOLLUTANTS FROM BLACK AND GREY WATER | 64 | ||
3.5 MULTI-CRITERIA ASSESSMENT ON ENVIRONMENTAL AND SOCIAL ASPECTS IN NEW SANITATION | 66 | ||
3.6 NEW SANITATION IN PRACTICE IN THE NETHERLANDS | 69 | ||
3.7 CONCLUSIONS | 73 | ||
3.8 REFERENCES | 73 | ||
Chapter 4: Wastewater treatment in algal systems | 76 | ||
4.1 INTRODUCTION | 76 | ||
4.2 FUNDAMENTALS OF MICROALGAE BASED SYSTEMS | 77 | ||
4.2.1 Photosynthetic aeration, symbiosis and algal-bacterial interactions | 77 | ||
4.2.2 Carbon, nitrogen and phosphorous removal mechanisms | 80 | ||
4.2.3 Strain selection | 81 | ||
4.2.4 Influence of environmental parameters | 82 | ||
4.3 MICROALGAE BASED SYSTEMS USED FOR WASTEWATER TREATMENT | 83 | ||
4.3.1 Bioreactors | 83 | ||
4.3.2 CO2 addition, implications in the process | 85 | ||
4.3.3 Harvesting of biomass | 86 | ||
4.4 CONSIDERATIONS FOR A REAL SCALE INSTALLATION | 89 | ||
4.5 CONCLUSIONS | 91 | ||
4.6 REFERENCES | 92 | ||
Chapter 5: Niches for bioelectrochemical systems in sewage treatment plants | 96 | ||
5.1 INTRODUCTION | 96 | ||
5.1.1 Microbial fuel cells | 97 | ||
5.1.2 Microbial electrolysis cell | 97 | ||
5.2 BES IN SEWAGE TREATMENT PLANTS | 98 | ||
5.2.1 Bioelectricity production | 98 | ||
5.2.2 Bioelectrochemical hydrogen production in WWTP | 100 | ||
5.2.3 Bioelectrochemical denitrification in WWTPs | 102 | ||
5.2.3.1 Nitrogen removal in WWTPs using BES | 102 | ||
5.2.3.2 Nitrogen recovery in WWTPs using BES | 103 | ||
5.3 CONCLUSIONS | 105 | ||
5.4 REFERENCES | 106 | ||
Part 1b: Reducing Space | 109 | ||
Chapter 6: Aerobic granular sludge reactors | 111 | ||
6.1 INTRODUCTION | 111 | ||
6.2 APPLICATIONS OF AEROBIC GRANULATION | 112 | ||
6.2.1 Industrial wastewater treatment | 112 | ||
6.2.2 Municipal wastewater treatment | 114 | ||
6.2.3 Toxic compounds degradation and biosorption of dyestuffs and heavy metals | 114 | ||
6.3 SCALE-UP: FROM THE LAB TO FULL SCALE | 116 | ||
6.4 CRITICAL ASPECTS | 119 | ||
6.5 MODELLING GRANULAR SLUDGE REACTORS | 121 | ||
6.5.1 Bioconversion processes | 121 | ||
6.5.2 Intragranule heterogeneity | 122 | ||
6.5.3 Intergranule heterogeneity | 123 | ||
6.5.4 Flow patterns inside the bulk fluid | 124 | ||
6.6 CONCLUSIONS | 124 | ||
6.7 REFERENCES | 125 | ||
Chapter 7: Membranes in wastewater treatment | 129 | ||
7.1 INTRODUCTION | 129 | ||
7.1.1 MBR’s when does it make sense? | 129 | ||
7.1.2 Energy demand reduction | 129 | ||
7.1.3 Enhanced nutrients and/or refractory compounds removal | 130 | ||
7.1.4 Synergistic effects utilization | 130 | ||
7.2 INNOVATIVE USE OF MEMBRANES IN WASTEWATER TREATMENT | 131 | ||
7.2.1 Anaerobic Membrane Bioreactors | 131 | ||
7.2.1.1 Feasibility for the treatment of different wastewater streams | 132 | ||
7.2.1.2 Barriers for widespread application | 132 | ||
7.2.1.3 Membrane fouling | 132 | ||
7.2.1.4 Fouling mitigation | 133 | ||
7.2.1.5 Mathematical modelling | 133 | ||
7.2.1.6 Life Cycle Cost (LCC) | 134 | ||
7.2.1.7 Life Cycle Assessment (LCA) | 134 | ||
7.2.1.8 Challenges and future perspectives for the use of AnMBRs | 135 | ||
7.2.2 Membranes for gas transfer | 135 | ||
7.2.2.1 Into what is different about membranes for gas transferring | 135 | ||
7.2.2.2 Types of membranes and configurations | 137 | ||
7.2.2.3 Potential advantageous uses of gas transferring membranes in an WWTP | 137 | ||
7.2.2.4 Challenges in the use of gas transferring membranes | 138 | ||
7.2.3 Microbial Desalination Cells (MDC) – anionic and cationic exchange membranes | 139 | ||
7.2.3.1 Principles and operation of MDCs | 140 | ||
7.2.3.2 Performance of MDCs | 141 | ||
7.2.3.3 Anionic and Cationic exchange membranes | 142 | ||
7.2.3.4 Challenges and future perspectives for the use of MFC’s | 144 | ||
7.3 CONCLUSIONS AND PERSPECTIVES | 145 | ||
7.4 REFERENCES | 150 | ||
Chapter 8: Enhanced primary treatment | 155 | ||
8.1 INTRODUCTION | 155 | ||
8.2 ENHANCED, HIGH-RATE PRIMARY TREATMENT | 156 | ||
8.2.1 Chemically enhanced primary treatment | 156 | ||
8.2.2 Microscreen-based technologies | 157 | ||
8.2.2.1 Rotating belt filters | 157 | ||
8.2.2.2 Rotating drum filters | 158 | ||
8.2.2.3 Rotating disc filters | 159 | ||
8.2.3 Vortex-based technologies | 159 | ||
8.2.4 Inclined-surface settlers | 160 | ||
8.3 PLANT-WIDE IMPACT OF ENHANCED PRIMARY PROCESSES | 165 | ||
8.3.1 Impact on secondary stage aeration demand | 165 | ||
8.3.2 Impact on production, properties, and anaerobic degradability of sludge | 165 | ||
8.3.3 Impact on nutrient removal | 168 | ||
8.3.4 Impact on power consumption and greenhouse gas emissions | 168 | ||
8.3.4.1 Calculation assumptions: | 169 | ||
8.4 MINI-ASSESSMENT | 174 | ||
8.5 REFERENCES | 174 | ||
Part 1c: Reducing Impacts | 177 | ||
Chapter 9: Innovative primary and secondary sewage treatment technologies for organic micropollutants abatement | 179 | ||
9.1 INTRODUCTION | 179 | ||
9.2 ENHANCEMENT OF PRIMARY AND SECONDARY SEWAGE TREATMENT FOR ORGANIC MICROPOLLUTANTS ELIMINATION | 183 | ||
9.2.1 Enhanced primary clarification | 183 | ||
9.2.2 Role of nitrifiers on organic micropollutants biotransformation | 185 | ||
9.2.3 Membrane bioreactors | 187 | ||
9.2.4 Granular sludge reactors | 191 | ||
9.2.5 Partial nitritation – Anammox process | 193 | ||
9.2.6 Anaerobic treatment | 195 | ||
9.2.7 Hybrid systems | 198 | ||
9.3 FATE OF TRANSFORMATION PRODUCTS DURING SEWAGE TREATMENT | 201 | ||
9.4 MODELLING MICROPOLLUTANTS FATE DURING SEWAGE TREATMENT | 205 | ||
9.5 CONCLUSION | 209 | ||
9.6 REFERENCES | 210 | ||
Chapter 10: Post-treatment for micropollutants removal | 214 | ||
10.1 INTRODUCTION | 214 | ||
10.2 CHEMICAL METHODS | 215 | ||
10.2.1 Ozonation | 215 | ||
10.2.2 Advanced Oxidation Processes | 218 | ||
10.3 PHYSICAL METHODS | 219 | ||
10.3.1 Adsorption to activated carbon | 219 | ||
10.3.1.1 PAC | 220 | ||
10.3.1.2 GAC | 224 | ||
10.3.2 Membrane filtration | 226 | ||
10.4 COSTS | 226 | ||
10.5 CONCLUSIONS | 228 | ||
10.6 REFERENCES | 229 | ||
Chapter 11: Technologies limiting gas and odour emissions | 233 | ||
11.1 INTRODUCTION | 233 | ||
11.2 PHYSICAL-CHEMICAL TECHNOLOGIES | 233 | ||
11.2.1 Absorption | 233 | ||
11.2.2 Adsorption | 235 | ||
11.2.3 Incineration | 237 | ||
11.2.4 Advantages and drawbacks of physical-chemical techniques | 238 | ||
11.3 MATURE BIOLOGICAL TECHNOLOGIES | 239 | ||
11.3.1 Biofilters | 239 | ||
11.3.2 Biotrickling filters | 240 | ||
11.3.3 Bioscrubbers | 242 | ||
11.3.4 Advantages and drawbacks of mature biological technologies | 243 | ||
11.4 EMERGING BIOLOGICAL TECHNOLOGIES | 243 | ||
11.4.1 Two-phase partitioning bioreactors | 243 | ||
11.4.2 Activated sludge diffusion | 245 | ||
11.4.3 Membrane bioreactors | 247 | ||
11.4.4 Activated sludge and oxidized ammonium recycling | 248 | ||
11.4.5 Advantages and drawbacks of emerging biological technologies | 249 | ||
11.5 CONCLUSIONS | 249 | ||
11.6 REFERENCES | 252 | ||
Chapter 12: Reducing the impact of sludge | 255 | ||
12.1 INTRODUCTION | 255 | ||
12.2 PROCESSES IN THE WATER LINE (A,B) | 257 | ||
12.2.1 Lysis-cryptic growth | 258 | ||
12.2.1.1 Chemical oxidation | 258 | ||
12.2.1.2 Enzymatic reactions | 258 | ||
12.2.1.3 Mechanical treatment | 259 | ||
12.2.2 Maintenance metabolism | 259 | ||
12.2.3 Uncoupling metabolism | 260 | ||
12.2.3.1 Chemical uncoupler | 260 | ||
12.2.3.2 Side stream anaerobic reactor | 261 | ||
12.2.4 Predation on bacteria | 261 | ||
12.3 PRE-TREATMENT PROCESSES IN THE SLUDGE LINE (C,D,E,F) | 262 | ||
12.3.1 Physical pre-treatments | 262 | ||
12.3.1.1 High pressure homogeneizers | 262 | ||
12.3.1.2 Ultrasonic treatment | 263 | ||
12.3.1.3 Grinding – Stirred ball mills | 263 | ||
12.3.1.4 Lysis centrifugation | 264 | ||
12.3.1.5 Focused-pulse technology | 264 | ||
12.3.1.6 Thermal hydrolysis | 264 | ||
12.3.1.7 Chemical oxidation | 265 | ||
12.3.1.8 Alkaline hydrolysis | 266 | ||
12.3.1.9 Biological pre-treatment | 266 | ||
12.4 TECHNOLOGIES FOR ENHANCING SLUDGE STABILIZATION (G) | 267 | ||
12.4.1 Thermophilic anaerobic digestion: effect of thermal pre-treatment | 267 | ||
12.4.2 Temperature-phased anaerobic digestion | 268 | ||
12.4.3 Sequential anaerobic-aerobic digestion of waste and mixed sludge | 271 | ||
12.5 WET OXIDATION OF SEWAGE SLUDGE COUPLED WITH ANAEROBIC DIGESTION OF LIQUID RESIDUE (H) | 273 | ||
12.5.1 Wet oxidation and its role in sewage sludge treatment | 273 | ||
12.5.2 WO of sewage sludge: effect of process parameters | 274 | ||
12.5.3 Reaction kinetics and process modelling | 275 | ||
12.5.4 Treatment/Disposal of residues | 275 | ||
12.6 COMPARATIVE ANALYSIS OF THE PROCESSES | 276 | ||
12.6.1 Enhanced hydrolysis. Processes in the sludge line | 277 | ||
12.6.2 Enhanced sludge stabilization processes | 278 | ||
12.7 REFERENCES | 279 | ||
Part 2: Re-using Water and Sludge | 283 | ||
Chapter 13: Producing high-quality recycled water | 285 | ||
13.1 INTRODUCTION | 285 | ||
13.2 WATER QUALITY CONSTITUENTS OF CONCERN AND REGULATORY REQUIREMENTS | 285 | ||
13.3 TREATMENT SCHEMES FOR POTABLE WATER REUSE | 287 | ||
13.4 ENERGY EFFICIENCY OF POTABLE WATER REUSE SCHEMES | 288 | ||
13.5 DESIGN REQUIREMENTS OF POTABLE WATER REUSE SCHEMES/ENERGY POTENTIAL | 290 | ||
13.6 STATE-OF-THE-ART WATER QUALITY MONITORING APPROACHES FOR HIGH-QUALITY RECYCLED WATER | 291 | ||
13.7 CONCLUSIONS | 294 | ||
13.8 REFERENCES | 294 | ||
Chapter 14: Producing sludge for agricultural applications | 296 | ||
14.1 INTRODUCTION | 296 | ||
14.2 SLUDGE PRODUCTION PROCESSES | 300 | ||
14.2.1 Sludge production | 301 | ||
14.2.1.1 Primary sludge production | 301 | ||
14.2.1.2 Biological sludge production | 301 | ||
14.2.2 Characteristics of sewage sludge | 303 | ||
14.3 SLUDGE PRE-TREATMENT PROCESSES | 304 | ||
14.3.1 Sludge pre-treatment technologies | 304 | ||
14.3.2 Effects of pretreatment on the agricultural use and value of sludge | 304 | ||
14.3.2.1 Organic Matter Reduction | 305 | ||
14.3.2.2 Nutrients Solubilization | 305 | ||
14.3.2.3 Pathogen and Indicator Reductions | 305 | ||
14.3.2.4 Trace Organic Contaminants Removal | 306 | ||
14.3.2.5 Heavy Metals | 306 | ||
14.4 SLUDGE TREATMENT PROCESSES | 307 | ||
14.4.1 Biological processes | 307 | ||
14.4.1.1 Anaerobic digestion | 307 | ||
14.4.1.2 Composting | 308 | ||
14.4.1.3 Vermicomposting | 309 | ||
14.4.1.4 Bioleaching | 309 | ||
14.4.2 Drying processes | 310 | ||
14.4.3 Thermal processes | 310 | ||
14.4.3.1 Incineration | 311 | ||
14.4.3.2 Pyrolysis and Gasification | 311 | ||
14.4.4 Chemical processes | 312 | ||
14.5 GENERAL EFFECTS OF BIOSOLIDS ON AGRICULTURE | 313 | ||
14.5.1 Effect on agricultural productivity and soil fertility | 313 | ||
14.5.2 Health risks involved in application of sludge in agriculture | 314 | ||
14.6 CASE STUDIES ON AGRICULTURAL APPLICATION OF SLUDGE | 316 | ||
14.7 CONCLUSIONS | 318 | ||
14.8 REFERENCES | 318 | ||
Part 3: Recovering Resource: Energy and Chemicals | 323 | ||
Chapter 15: Recovering energy from sludge | 325 | ||
15.1 INTRODUCTION | 325 | ||
15.1.1 Sewage sludge definition and production | 326 | ||
15.1.2 Legislation issues applied to SS and current status | 327 | ||
15.1.3 Legislative constraints and policy goals | 329 | ||
15.2 BIOLOGICAL BASED TECHNOLOGIES | 330 | ||
15.2.1 Advanced thermal/high pressure pre-treatments to enhance energy recovery in AD processes | 330 | ||
15.2.1.1 General features and technology basis | 330 | ||
15.2.1.2 Commercial thermal pre-treatments comparison | 331 | ||
15.2.1.3 Economic evaluation | 332 | ||
15.2.2 Co-digestion of sewage sludge with non-sludge organic wastes | 333 | ||
15.2.3 Bio-drying of sewage sludge to produce biomass fuel | 337 | ||
15.3 THERMAL BASED TECHNOLOGIES | 340 | ||
15.3.1 Gasification | 340 | ||
15.3.2 Pyrolysis | 342 | ||
15.3.3 Supercritical water processing | 344 | ||
15.4 CONCLUSIONS | 348 | ||
15.5 REFERENCES | 352 | ||
Chapter 16: Metal recovery from sludge: Problem or opportunity | 355 | ||
16.1 INTRODUCTION | 355 | ||
16.2 LEACHING OF METALS FROM SLUDGE | 358 | ||
16.2.1 Chemical leaching | 358 | ||
16.2.2 Bioleaching | 358 | ||
16.3 REMOVAL OF METAL FROM THE LEACHATE WITHOUT METAL RECOVERY | 359 | ||
16.3.1 Metal precipitation | 359 | ||
16.3.2 Metal adsorption | 361 | ||
16.4 METAL RECOVERY | 362 | ||
16.4.1 Removal of impurities from leach solution | 362 | ||
16.4.2 Metal separation | 362 | ||
16.4.2.1 Liquid- liquid extraction | 362 | ||
16.4.2.2 Electrodialysis | 363 | ||
16.4.2.3 Membrane filtration | 364 | ||
16.4.3 Metal recovery technologies | 364 | ||
16.4.3.1 Electrowinning | 364 | ||
16.4.3.2 Bio electrochemical methods | 365 | ||
16.5 USE OF SLUDGE AFTER CHEMICAL LEACHING OR BIOLEACHING | 366 | ||
16.6 CONCLUSIONS | 366 | ||
16.7 REFERENCES | 367 | ||
Chapter 17: Nutrients recovery from wastewater streams | 369 | ||
17.1 INTRODUCTION | 369 | ||
17.2 RECOVERY OF AMMONIA BASED PRODUCTS | 370 | ||
17.2.1 Processes | 370 | ||
17.2.1.1 Air stripping | 370 | ||
17.2.1.2 Steam stripping | 371 | ||
17.2.1.3 Membrane processes | 373 | ||
17.2.2 Products | 374 | ||
17.2.2.1 Ammonium sulphate | 374 | ||
17.2.2.2 Ammonia water | 375 | ||
17.2.2.3 Ammonium nitrate | 375 | ||
17.3 RECOVERY OF PHOSPHORUS BASED PRODUCTS | 377 | ||
17.3.1 Struvite | 377 | ||
17.3.1.1 Production process and existing experience | 378 | ||
17.3.1.2 Struvite production in full-scale installations | 380 | ||
17.3.1.3 Novel processes for struvite production based on biological processes | 381 | ||
17.3.1.4 Product end-uses | 383 | ||
17.3.2 Potassium phosphate | 383 | ||
17.3.2.1 Production process and existing experience | 383 | ||
17.3.2.2 Lab-scale experience on synthetic and real urine | 383 | ||
17.3.2.3 Full-scale implementation on calf manure | 384 | ||
17.3.2.4 Product end-uses | 384 | ||
17.3.2.5 Future perspectives | 384 | ||
17.3.3 Calcium phosphate and hydroxyapatite | 385 | ||
17.3.3.1 Production process and existing experience | 385 | ||
17.3.3.2 Product end-uses | 385 | ||
17.3.4 Recovery of phosphorus compounds from sludge ashes | 386 | ||
17.3.4.1 Thermochemical processes | 387 | ||
17.3.4.2 Wet-chemical processes | 390 | ||
17.3.4.3 Future perspectives | 392 | ||
17.4 CONCLUSIONS | 394 | ||
17.5 REFERENCES | 394 | ||
Chapter 18: Recovery of organic added value products from wastewater | 399 | ||
18.1 INTRODUCTION | 399 | ||
18.1.1 Potential feedstocks in wastewater treatment plants | 399 | ||
18.1.2 Most studied processes | 401 | ||
18.1.2.1 Acids and alcohols | 401 | ||
18.1.2.2 Biopolymers | 403 | ||
18.1.2.3 Methane | 403 | ||
18.2 PROCESSES AND TECHNOLOGIES | 403 | ||
18.2.1 Acids and alcohols | 403 | ||
18.2.2 PHA | 405 | ||
18.2.3 Reported pilot/demonstration/industrial scale plants | 406 | ||
18.3 QUANTITY, QUALITY AND APPLICATIONS | 408 | ||
18.3.1 PHA | 408 | ||
18.3.1.1 Feedstock requirements for sustainable productivity | 408 | ||
18.3.1.2 Effects of operation parameters on polymer quality | 409 | ||
18.3.1.3 Applications depending on polymer quality | 410 | ||
18.3.2 Acids and alcohols | 412 | ||
18.3.2.1 Feedstock requirements for sustainable productivity | 412 | ||
18.3.2.2 Effects of operation parameters | 412 | ||
18.3.2.3 Applications depending on acid and alcohols quality | 414 | ||
18.4 FUTURE PERSPECTIVES | 415 | ||
18.5 CONCLUSIONS | 416 | ||
18.6 REFERENCES | 417 | ||
Part 4: Economic, Environmental, Legal and Social Impacts | 421 | ||
Chapter 19: The impact of innovation on wastewater treatment economics | 423 | ||
19.1 INTRODUCTION | 423 | ||
19.2 COSTS OF IMPROVING/INNOVATION IN WWTPs | 424 | ||
19.2.1 Internal costs | 424 | ||
19.2.1.1 Engineering approach | 424 | ||
19.2.1.2 Parametric approach | 425 | ||
19.2.1.3 Case studies | 425 | ||
19.2.2 External costs | 427 | ||
19.3 BENEFITS OF IMPROVING/INNOVATION IN WWTPs | 428 | ||
19.3.1 Internal benefit | 428 | ||
19.3.2 External benefit | 428 | ||
19.3.2.1 Conventional valuation methods | 429 | ||
19.3.2.2 Shadow price of pollutants | 429 | ||
19.3.2.3 Case studies | 430 | ||
19.4 NET PRESENT VALUE | 431 | ||
19.5 FUNDING OPPORTUNITIES | 431 | ||
19.6 CONCLUSIONS | 433 | ||
19.7 REFERENCES | 434 | ||
Chapter 20: Assessing environmental impacts and benefits of wastewater treatment plants | 437 | ||
20.1 INTRODUCTION | 437 | ||
20.2 APPLICATION OF LIFE CYCLE ASSESSMENT TO WASTEWATER TREATMENT PLANTS AND PROCESSES | 441 | ||
a) Goal and scope definition | 442 | ||
b) Life cycle inventory | 443 | ||
c) Life Cycle Impact Assessment | 444 | ||
d) Interpretation and communication of LCA results | 445 | ||
20.3 CASE STUDIES | 446 | ||
20.3.1 Fact sheet: LCA of conventional WWTP | 446 | ||
20.3.1.1 Goal and scope definition | 446 | ||
20.3.2 Fact sheet: LCA study on WWTP upgrade for elimination of organic micropollutants | 449 | ||
20.3.2.1 Goal and scope definition | 449 | ||
20.3.3 Fact sheet: Simplified LCA study focussing on operational energy demand and greenhouse gas emissions of a new energy-positive wastewater treatment scheme | 450 | ||
20.3.3.1 Goal and scope definition | 451 | ||
20.3.4 Fact sheet: LCA study on phosphorus recovery from sewage sludge, sludge liquor, or incineration ash | 453 | ||
20.3.4.1 Goal and scope definition | 453 | ||
20.4 CONCLUSIONS AND OUTLOOK | 456 | ||
20.5 REFERENCES | 456 | ||
Chapter 21: Determining benchmarks in wastewater treatment plants using life cycle assessment | 459 | ||
21.1 INTRODUCTION | 459 | ||
21.2 JOINT APPLICATION OF LIFE CYCLE ASSESSMENT AND DATA ENVELOPMENT ANALYSIS TO WASTEWATER TREATMENT PROCESSES | 460 | ||
21.3 MATERIALS AND METHODS | 461 | ||
21.3.1 The five-step LCA + DEA method | 461 | ||
21.3.2 DEA model selection and matrices build up | 462 | ||
21.4 RESULTS AND DISCUSSION | 463 | ||
21.4.1 Inventory data and DEA computation | 463 | ||
21.4.2 Environmental and operational performance | 463 | ||
21.4.3 Factors affecting WWTPs efficiency | 465 | ||
21.5 CONCLUSIONS | 466 | ||
21.6 REFERENCES | 466 | ||
Chapter 22: Public perceptions of recycled water | 468 | ||
22.1 INTRODUCTION | 468 | ||
22.1.1 Public perceptions – a road block on the journey to recycled water schemes? | 468 | ||
22.1.2 How perceptions are formed – the importance of emotions | 468 | ||
22.1.3 Importance of considering public perceptions | 469 | ||
22.2 WHAT DO THE PUBLIC THINK ABOUT RECYCLED WATER? | 469 | ||
22.2.1 Are people willing to use recycled water? | 469 | ||
22.2.1.1 The role of context – different levels of support for different types of water uses | 470 | ||
22.2.1.2 The role of language – different levels of support for different types of descriptions | 471 | ||
22.2.2 Why are some people unwilling to use recycled water? | 471 | ||
22.2.2.1 Association with sewage and human waste | 471 | ||
22.2.2.2 General safety and health risks | 472 | ||
22.2.2.3 Microbial and chemical contamination | 472 | ||
22.2.2.4 Aesthetic features – colour, taste and odour | 472 | ||
22.2.2.5 Environmental benefits and impacts | 473 | ||
22.2.2.6 Price | 473 | ||
22.3 WHAT INFLUENCES PERCEPTIONS ABOUT RECYCLED WATER? | 473 | ||
22.3.1 Socio-demographics | 474 | ||
22.3.1.1 Gender | 474 | ||
22.3.1.2 Age | 475 | ||
22.3.1.3 Education | 475 | ||
22.3.2 Experience of water shortages | 475 | ||
22.3.3 Knowledge | 476 | ||
22.3.4 Exposure to information and expertise | 476 | ||
22.3.5 Trust in institutions and technology | 477 | ||
22.3.5.1 Organisational trust – governments and water authorities | 477 | ||
22.3.5.2 Scientific trust – water-treatment technology and scientists | 477 | ||
22.3.6 Values and social norms | 477 | ||
22.3.6.1 Environmental values | 478 | ||
22.3.6.2 Social norms | 478 | ||
22.4 INTERVENING TO IMPROVE PUBLIC PERCEPTIONS OF RECYCLED WATER | 478 | ||
22.4.1 Providing information | 478 | ||
22.4.2 Psychological approaches to communication | 479 | ||
22.4.3 Community dialogue | 480 | ||
22.4.3.1 Dialogue targeting risk perceptions | 480 | ||
22.4.3.2 Dialogue targeting community needs | 481 | ||
22.4.4 Ensure fair and transparent processes for planning and decision making | 481 | ||
22.4.5 Provide opportunities to experience recycled water | 482 | ||
22.4.6 Building public support – features of successful programs | 482 | ||
22.4.6.1 Groundwater Replenishment System – Orange County Water District, United States | 483 | ||
22.4.6.2 Aquifer recharge trial – Perth, Australia | 483 | ||
22.4.6.3 Introduction of NEWater – Singapore | 484 | ||
22.5 CONCLUSIONS | 485 | ||
22.6 REFERENCES | 485 | ||
Chapter 23: Greenhouse and odour emissions | 488 | ||
23.1 GREENHOUSE GAS EMISSIONS DURING WASTEWATER TREATMENT | 488 | ||
23.1.1 Introduction | 488 | ||
23.1.2 Operational factors affecting direct GHG emissions during wastewater treatment | 489 | ||
23.1.2.1 Factors affecting N2O production during aerobic conditions by nitrifiers | 489 | ||
23.1.2.2 Factors affecting N2O production during anoxic conditions by denitrifiers | 491 | ||
23.1.2.3 Factors affecting CH4 production | 492 | ||
23.1.3 GHG monitoring methodologies | 493 | ||
23.1.3.1 The Floating hood + gas analyser approach | 493 | ||
23.1.3.2 Estimating N2O emissions through N2O dissolved data | 495 | ||
23.1.3.3 Plant integrated measurements | 496 | ||
23.1.4 Mitigation of direct GHG emissions | 496 | ||
23.2 ODOUR EMISSIONS DURING WASTEWATER TREATMENT | 497 | ||
23.2.1 Introduction | 497 | ||
23.2.2 Odour characterization: sensorial and chemical analysis | 499 | ||
23.2.2.1 Analytical techniques | 499 | ||
23.2.2.2 Sensorial techniques | 500 | ||
23.2.2.3 Mixed sensorial and analytical techniques | 501 | ||
23.2.2.4 Field and laboratory applications of analytical and sensorial techniques | 501 | ||
23.2.3 Impact assessment | 502 | ||
23.2.3.1 Measuring odour impact at the receptor location | 502 | ||
23.2.3.2 Evaluation of odour impact from source by dispersion modelling | 502 | ||
23.2.3.3 Odour impact assessment | 503 | ||
23.2.4 Minimization, mitigation and treatment of odourous emissions | 503 | ||
23.2.4.1 Minimization of odour formation | 503 | ||
23.2.4.2 Impact minimization | 505 | ||
23.2.4.3 Odour abatement | 505 | ||
23.3 CONCLUSIONS | 506 | ||
23.4 REFERENCES | 506 | ||
Chapter 24: The impact and risks of micropollutants in the environment | 510 | ||
24.1 INTRODUCTION | 510 | ||
24.2 LEGAL AND ANALYTICAL ASPECTS | 513 | ||
24.3 OCCURRENCE OF MICROPOLLUTANTS IN TREATED EFFLUENTS, SLUDGE, SURFACE AND GROUND WATER | 514 | ||
24.4 FATE OF SELECTED COMPOUNDS | 517 | ||
24.4.1 Biodegradation | 518 | ||
24.4.2 Sorption | 519 | ||
24.4.3 Photodegradation: direct and indirect | 520 | ||
24.4.4 Hydrolysis | 521 | ||
24.5 ECOTOXICOLOGICAL ASPECTS | 521 | ||
24.5.1 Whole effects approach | 524 | ||
24.5.1.1 Estrogenic activity | 524 | ||
24.5.1.2 Mutagenic activity | 526 | ||
24.6 RISK ASSESSMENT OF MICROPOLLUTANTS: THE MOST CRITICAL COMPOUNDS | 526 | ||
24.7 FINAL REMARKS AND CONCLUSIONS | 528 | ||
24.8 REFERENCES | 530 | ||
Chapter 25: Legal and policy frameworks for the management of wastewater | 534 | ||
25.1 INTRODUCTION | 534 | ||
25.1.1 Structures for ownership and regulation | 535 | ||
25.1.2 Regulation and liability | 535 | ||
25.2 REGULATION OF WASTEWATER TREATMENT FACILITIES | 536 | ||
25.2.1 General environmental law | 536 | ||
25.2.2 Specific regulation of wastewater treatment | 537 | ||
25.2.2.1 The European Union urban waste water treatment directive | 537 | ||
25.2.2.2 The USA | 538 | ||
25.2.2.3 Canada | 538 | ||
25.2.2.4 Trade effluents | 539 | ||
25.3 REGULATION OF ONSITE SANITATION | 539 | ||
25.3.1 Impacts on groundwater | 540 | ||
25.4 SLUDGE DISPOSAL AND REUSE | 541 | ||
25.4.1 Solid waste disposal | 541 | ||
25.4.2 Agricultural use | 541 | ||
25.4.3 Marine wastewater discharge from vessels | 542 | ||
25.5 REUSE OF WASTEWATER | 543 | ||
25.5.1 Regulation of greywater reuse | 544 | ||
25.5.2 Reuse as drinking water | 545 | ||
25.6 CLIMATE CHANGE AND ENERGY IN THE WASTEWATER SECTOR | 546 | ||
25.6.1 Mitigation considerations | 546 | ||
25.6.2 Adaptation considerations | 547 | ||
25.7 REGULATION OF CONTAMINANTS OF EMERGING CONCERN | 548 | ||
25.8 CONCLUSIONS | 549 | ||
25.9 REFERENCES | 549 | ||
Part 5: Conceiving, Comparing and Selecting Efficient Processes | 553 | ||
Chapter 26: Environmental decision support systems | 555 | ||
26.1 INTRODUCTION | 555 | ||
26.2 LEVELS OF DECISION | 556 | ||
26.3 COMPLEXITY OF THE DECISIONS | 557 | ||
26.4 WHAT IS AN EDSS? | 559 | ||
26.5 WHY USING AN EDSS? | 560 | ||
26.6 HOW TO BUILD AN EDSS? | 561 | ||
26.7 NOVEDAR_EDSS: AN EDSS FOR SELECTION OF WWTP CONFIGURATIONS | 562 | ||
26.8 NOVEDARPLUS_EDSS: AN EDSS FOR THE ‘3R’ PARADIGM | 564 | ||
26.9 CASE STUDIES | 566 | ||
26.9.1 Case study | 568 | ||
Objective | 568 | ||
Scenario definition | 568 | ||
Results | 568 | ||
Analysis performed under different criteria | 570 | ||
Results under different conditions | 570 | ||
Influent conditions | 570 | ||
Effluent requirements | 570 | ||
Conclusion | 571 | ||
26.9.2 Case study | 571 | ||
Objective | 572 | ||
Scenario definition | 572 | ||
Results | 573 | ||
Conclusion | 575 | ||
26.9.3 Case study | 575 | ||
Objective | 575 | ||
Scenario definition | 577 | ||
Results | 577 | ||
Shortlist selection of alternatives | 578 | ||
26.10 CONCLUSIONS | 579 | ||
26.11 REFERENCES | 580 | ||
Chapter 27: Superstructure-based optimization tool for plant design and retrofitting | 581 | ||
27.1 INTRODUCTION | 581 | ||
27.2 SUPERSTRUCTURE-BASED OPTIMIZATION FRAMEWORK | 582 | ||
27.3 CASE STUDY APPLICATION | 587 | ||
27.4 CONCLUSIONS AND FUTURE PERSPECTIVES | 597 | ||
27.5 REFERENCES | 597 | ||
Chapter 28: Model-based comparative assessment of innovative processes | 599 | ||
28.1 INTRODUCTION | 599 | ||
28.2 E-PWM METHODOLOGY | 600 | ||
28.2.1 Category selection | 600 | ||
28.2.2 Unit-process models selection | 601 | ||
28.2.3 Actuator models selection | 604 | ||
28.2.4 Evaluation criteria | 604 | ||
28.3 MODEL-BASED COMPARATIVE ASSESSMENT OF CONVENTIONAL AND INNOVATIVE PLANT LAYOUTS | 607 | ||
28.3.1 Conventional WWTP | 608 | ||
28.3.2 Upgraded WWTP | 609 | ||
28.3.3 A new WWT concept: C/N/P decoupling WWTP | 611 | ||
28.4 MODEL BASED ANALYSIS AND OPTIMISATION OF PLANT OPERATION | 613 | ||
28.5 CASE STUDY DEMONSTRATION: ANALYSIS AND OPTIMISATION OF A CONVENTIONAL WASTEWATER TREATMENT PLANT | 614 | ||
Step 1: Definition of the operational objective and requirements | 614 | ||
Step 2: Determination of the degrees of freedom for operation and control | 614 | ||
Step 3: Study the effect of the degrees of freedom on the objectives and the constraints | 615 | ||
Step 4: Match the degrees of freedom with the constraints | 618 | ||
Step 5: Use the remaining degrees of freedom to optimise the process | 619 | ||
28.6 CONCLUSIONS | 619 | ||
28.7 REFERENCES | 620 | ||
Annex 1: E-course: Micropollutants in water | 622 | ||
Annex 2: Implementing an ecoefficiency tool for the holistic design and assessment of the water cycle | 625 | ||
A2.1 INTRODUCTION | 625 | ||
A2.2 TOOL FEATURES | 626 | ||
A2.3 DRINKING WATER TREATMENT PLANT (DWTP) | 627 | ||
A2.4 SUPPLY NETWORK | 628 | ||
A2.5 SEWER NETWORK | 630 | ||
A2.6 WASTEWATER TREATMENT PLANT (WWTP) | 630 | ||
A2.7 VIEWING THE RESULTS OF A PROJECT | 631 | ||
Annex 3: NOVEDAR_EDSS: Intelligent/expert screening of process technologies | 635 | ||
A3.1 INTRODUCTION | 635 | ||
A3.2 PROBLEM DEFINITION | 636 | ||
A3.3 ALTERNATIVE GENERATION | 640 | ||
A3.4 ALTERNATIVE EVALUATION | 642 | ||
A3.5 NEW FEATURES AND CHARACTERISTICS: NOVEDARPLUS_EDSS | 644 | ||
Index | 648 |