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Handbook of biological wastewater treatment : design and optimisation of activated sludge systems / A.C. van Haandel and J.G.M. van der Lubbe.
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Title:Handbook of biological wastewater treatment : design and optimisation of activated sludge systems / A.C. van Haandel and J.G.M. van der Lubbe.
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Author/Creator:Haandel, Adrianus C. van.
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Other Contributors/Collections:Lubbe, J. G. M. van der.
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Published/Created:London ; New York : IWA Pub., 2012.
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Holdings
Holdings Record Display
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Location:WOODWARD LIBRARY stacksWhere is this?
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Call Number: TD756 .H236 2012
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Number of Items:1
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Status:Available
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Links:Donor bookplate
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Location:WOODWARD LIBRARY stacksWhere is this?
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Library of Congress Subjects:Sewage--Purification--Biological treatment--Handbooks, manuals, etc.
Sewage--Purification--Activated sludge process--Handbooks, manuals, etc.
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Medical Subjects: Sewage--purification.
Sewage--biological treatment.
Sewage--activated sludge process.
Waste Disposal, Fluid
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Edition:2nd ed.
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Description:xlvi, 770 pages : illustrations ; 26 cm.
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Notes:Includes bibliographical references (pages [671]-684).
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ISBN:9781780400006 (cased)
1780400004 (cased)
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Contents:Machine generated contents note: ch. 1 Scope of text
1.0. Introduction
1.1. Advances in secondary wastewater treatment
1.2. Tertiary wastewater treatment
1.3. Temperature influence on activated sludge design
1.4. Objective of the text
ch. 2 Organic material and bacterial metabolism
2.0. Introduction
2.1. Measurement of organic material
2.1.1. COD test
2.1.2. BOD test
2.1.3. TOC test
2.2. Comparison of measurement parameters
2.3. Metabolism
2.3.1. Oxidative metabolism
2.3.2. Anoxic respiration
2.3.3. Anaerobic digestion
ch. 3 Organic material removal
3.0. Introduction
3.1. Organic material and activated sludge composition
3.1.1. Organic material fractions in wastewater
3.1.2. Activated sludge composition
3.1.2.1. Active sludge
3.1.2.2. Inactive sludge
3.1.2.3. Inorganic sludge
3.1.2.4. Definition of sludge fractions
3.1.3. Mass balance of the organic material
3.2. Model notation
3.3. Steady-state model of the activated sludge system
3.3.1. Model development
3.3.1.1. Definition of sludge age
3.3.1.2. COD fraction discharged with the effluent
3.3.1.3. COD fraction in the excess sludge
3.3.1.4. COD fraction oxidised for respiration
3.3.1.5. Model summary and evaluation
3.3.2. Model calibration
3.3.3. Model applications
3.3.3.1. Sludge mass and composition
3.3.3.2. Biological reactor volume
3.3.3.3. Excess sludge production and nutrient demand
3.3.3.4. Temperature effect
3.3.3.5. True yield versus apparent yield
3.3.3.6. F/M ratio
3.3.4. Selection and control of the sludge age
3.4. General model of the activated sludge system
3.4.1. Model development
3.4.2. Model calibration
3.4.3. Application of the general model
3.5. Configurations of the activated sludge system
3.5.1. Conventional activated sludge systems
3.5.2. Sequential batch systems
3.5.3. Carrousels
3.5.4. Aerated lagoons
ch. 4 Aeration
4.0. Introduction
4.1. Aeration theory
4.1.1. Factors affecting kla and DOs
4.1.2. Effect of local pressure on DOs
4.1.3. Effect of temperature on kla and DOs
4.1.4. Oxygen transfer efficiency for surface aerators
4.1.5. Power requirement for diffused aeration
4.2. Methods to determine the oxygen transfer efficiency
4.2.1. Determination of the standard oxygen transfer efficiency
4.2.2. Determination of the actual oxygen transfer efficiency
ch. 5 Nitrogen removal
5.0. Introduction
5.1. Fundamentals of nitrogen removal
5.1.1. Forms and reactions of nitrogenous matter
5.1.2. Mass balance of nitrogenous matter
5.1.3. Stoichiometrics of reactions with nitrogenous matter
5.1.3.1. Oxygen consumption
5.1.3.2. Effects on alkalinity
5.1.3.3. Effects on pH
5.2. Nitrification
5.2.1. Nitrification kinetics
5.2.2. Nitrification in systems with non aerated zones
5.2.3. Nitrification potential and nitrification capacity
5.2.4. Design procedure for nitrification
5.3. Denitrification
5.3.1. System configurations for denitrification
5.3.1.1. Denitrification with an external carbon source
5.3.1.2. Denitrification with an internal carbon source
5.3.2. Denitrification kinetics
5.3.2.1. Sludge production in anoxic/aerobic systems
5.3.2.2. Denitrification rates
5.3.2.3. Minimum anoxic mass fraction in the pre-D reactor
5.3.3. Denitrification capacity
5.3.3.1. Denitrification capacity in a pre-D reactor
5.3.3.2. Denitrification capacity in a post-D reactor
5.3.4. Available nitrate
5.4. Designing and optimising nitrogen removal
5.4.1. Calculation of nitrogen removal capacity
5.4.2. Optimised design of nitrogen removal
5.4.2.1. Complete nitrogen removal
5.4.2.2. Incomplete nitrogen removal
5.4.2.3. Effect of recirculation of oxygen on denitrification capacity
5.4.2.4. Design procedure for optimized nitrogen removal
ch. 6 Innovative systems for nitrogen removal
6.0. Introduction
6.1. Nitrogen removal over nitrite
6.1.1. Basic principles of nitritation
6.1.2. Kinetics of high rate ammonium oxidation
6.1.3. Reactor configuration and operation
6.1.4. Required model enhancements
6.2. Anaerobic ammonium oxidation
6.2.1. Anammox process characteristics
6.2.2. Reactor design and configuration
6.3. Combination of nitritation with anammox
6.3.1. Two stage configuration (nitritation reactor
-Anammox)
6.3.2. Case study: full scale SHARON
- Anammox treatment
6.3.3. Single reactor configurations
6.4. Bioaugmentation
6.5. Side stream nitrogen removal: evaluation and potential
ch. 7 Phosphorus removal
7.0. Introduction
7.1. Biological Phosphorus Removal
7.1.1. Mechanisms involved in biological phosphorus removal
7.1.2. Bio-P removal system configurations
7.1.3. Model of biological phosphorus removal
7.1.3.1. Enhanced cultures
7.1.3.2. Mixed cultures
7.1.3.3. Denitrification of bio-P organisms
7.1.3.4. Discharge of organic phosphorus with the effluent
7.2. Optimisation of biological nutrient removal
7.2.1. Influence of wastewater characteristics
7.2.2. Improving substrate availability for nutrient removal
7.2.3. Optimisation of operational conditions
7.2.4. Resolving operational problems
7.3. Chemical phosphorus removal
7.3.1. Stoichiometrics of chemical phosphorus removal
7.3.1.1. Addition of metal salts
7.3.1.2. Addition of lime
7.3.1.3. Effects on pH
7.3.2. Chemical phosphorus removal configurations
7.3.2.1. Pre-precipitation
7.3.2.2. Simultaneous precipitation
7.3.2.3. Post-precipitation
7.3.2.4. Sidestream precipitation
7.3.3. Design procedure for chemical phosphorus removal
ch. 8 Sludge settling
8.0. Introduction
8.1. Methods to determine sludge settleability
8.1.1. Zone settling rate test
8.1.2. Alternative parameters for sludge settleability
8.1.3. Relationships between different settleability parameters
8.2. Model for settling in a continuous settler
8.2.1. Determination of the limiting concentration Xl
8.2.2. Determination of the critical concentration Xc
8.2.3. Determination of the minimum concentration Xm
8.3. Design of final settlers
8.3.1. Optimised design procedure for final settlers
8.3.2. Determination of the critical recirculation rate
8.3.3. Graphical optimization of final settler operation
8.3.4. Optimisation of the system of biological reactor and final settler
8.3.5. Validation of the optimised settler design procedure
8.3.5.1. US EPA design guidelines
8.3.5.2. WRC and modified WRC design guidelines
8.3.5.3. STORA/STOWA design guidelines
8.3.5.4. ATV design guidelines
8.3.5.5. Solids flux compared with other design methods
8.4. Physical design aspects for final settlers
8.5. Final settlers under variable loading conditions
ch. 9 Sludge bulking and scum formation
9.0. Introduction
9.1. Microbial aspects of sludge bulking
9.2. Causes and control of sludge bulking
9.2.1. Sludge bulking due to a low reactor substrate concentration
9.2.2. Guidelines for selector design
9.2.3. Control of bulking sludge in anoxic-aerobic systems
9.2.4. Other causes of sludge bulking
9.3. Non-specific measures to control sludge bulking
9.4. Causes and control of scum formation
ch. 10 Membrane bioreactors
10.0. Introduction
10.1. Membrane bioreactors (MBR)
10.2. MBR configurations
10.2.1. Submerged MBR
10.2.2. Cross-flow MBR
10.2.3. Comparison of submerged and cross-flow MBR
10.3. MBR design considerations
10.3.1. Theoretical concepts in membrane filtration
10.3.2. Impact on activated sludge system design
10.3.3. Pre-treatment
10.3.4. Module configuration
- submerged MBR
10.3.5. Module aeration
- submerged MBR
10.3.6. Key design data of different membrane types
10.4. MBR operation
10.4.1. Operation of submerged membranes
10.4.2. Operation of cross-flow membranes
10.4.3. Membrane fouling
10.4.4. Membrane cleaning
10.5. MBR technology: evaluation and potential
ch. 11 Moving bed biofilm reactors
11.0. Introduction
11.1. MBBR technology and reactor configuration
11.1.1. Carriers used in MBBR processes
11.1.2. Aeration system
11.1.3. Sieves and mixers
11.2. Features of MBBR process
11.3. MBBR process configurations
11.3.1. Pure MBBR
11.3.2. MBBR as pre-treatment
11.3.3. MBBR as post-treatment
11.3.4. Integrated fixed film reactors
11.4. Pure MBBR design and performance
11.4.1. Secondary treatment of municipal sewage
11.4.2. Secondary treatment of industrial wastewater
11.4.3. Nitrification
11.4.4. Nitrogen removal
11.4.5. Phosphorus removal
11.5. Upgrading of existing activated sludge plants
11.5.1. High rate pre-treatment MBBR for BOD/COD removal
11.5.2. Upgrading of secondary CAS to nitrification
11.5.3. Nitrification in IFAS processes
11.5.4. IFAS for nitrogen removal
11.6. Solids removal from MBBR effluent
11.6.1. Gravity settling
11.6.2. Micro-sand ballasted lamella sedimentation
11.6.3. Dissolved air flotation
11.6.4. Micro screening
11.6.5. Media filtration
11.6.6. Membrane filtration
ch. 12 Sludge treatment and disposal
Contents note continued: 12.0. Introduction
12.1. Excess sludge quality and quantity
12.2. Sludge thickeners
12.2.1. Design of sludge thickeners using the solids flux theory
12.2.2. Design of sludge thickeners using empirical relationships
12.3. Aerobic digestion
12.3.1. Kinetic model for aerobic sludge digestion
12.3.1.1. Variation of the volatile sludge concentration
12.3.1.2. Variation of the oxygen uptake rate
12.3.1.3. Variation of the nitrate concentration
12.3.1.4. Variation of the alkalinity
12.3.1.5. Variation of the BOD
12.3.2. Aerobic digestion in the main activated sludge process
12.3.3. Aerobic digester design
12.3.4. Optimisation of aerobic sludge digestion
12.3.5. Operational parameters of the aerobic digester
12.4. Anaerobic digestion
12.4.1. Stoichiometry of anaerobic digestion
12.4.2. Configurations used for anaerobic digestion
12.4.3. Influence of operational parameters
12.4.4. Performance of the high rate anaerobic digester
12.4.4.1. Removal efficiency of volatile suspended solids
12.4.4.2. Biogas production
12.4.4.3. Energy generation in anaerobic sludge digesters
12.4.4.4. Solids destruction and stabilised excess sludge production
12.4.4.5. Nutrient balance in the anaerobic digester
12.4.5. Design and optimisation of anaerobic digesters
12.5. Stabilised sludge drying and disposal
12.5.1. Natural sludge drying
12.5.2. Design and optimisation of natural sludge drying beds
12.5.2.1. Determination of the percolation time (t2)
12.5.2.2. Determination of the evaporation time (t4)
12.5.2.3. Influence of rain on sludge drying bed productivity
12.5.3. Accelerated sludge drying with external energy
12.5.3.1. Use of solar energy
12.5.3.2. Use of combustion heat from biogas
ch. 13 Anaerobic pretreatment
13.0. Introduction
13.1. Anaerobic treatment of municipal sewage
13.1.1. Configurations for anaerobic sewage treatment
13.1.1.1. Anaerobic filter
13.1.1.2. Fluidised and expanded bed systems
13.1.1.3. Upflow anaerobic sludge blanket (UASB) reactor
13.1.1.4. RALF system
13.1.2. Evaluation of different anaerobic configurations
13.2. Factors affecting municipal UASB performance
13.2.1. Design and engineering issues
13.2.2. Operational-and maintenance issues
13.2.3. Inappropriate expectations of UASB performance
13.2.4. Presence of sulphate in municipal sewage
13.2.5. Energy production and greenhouse gas emissions
13.2.5.1. Carbon footprint
13.2.5.2. Biogas utilization
13.3. Design model for anaerobic sewage treatment
13.3.1. Sludge age as the key design parameter
13.3.2. Influence of the temperature
13.3.3. Characterisation of anaerobic biomass
13.4. UASB reactor design guidelines
13.5. Post-treatment of anaerobic effluent
13.5.1. Secondary treatment of anaerobic effluent
13.5.1.1. Applicability of the ideal steady state model for COD removal
13.5.1.2. Stabilisation of aerobic excess sludge in the UASB reactor
13.5.2. Nitrogen removal from anaerobic effluent
13.5.2.1. Bypass of raw sewage to the activated sludge system
13.5.2.2. Anaerobic digestion with reduced methanogenic efficiency
13.5.2.3. Application of innovative nitrogen removal configurations
13.5.3. Future developments
13.5.3.1. Two stage anaerobic digestion
13.5.3.2. Psychrophilic anaerobic wastewater treatment
13.6. Anaerobic treatment of industrial wastewater
ch. 14 Integrated cost-based design and operation
14.0. Introduction
14.1. Preparations for system design
14.1.1. basis of design
14.1.1.1. Wastewater characteristics
14.1.1.2. Kinetic parameters and settleability of the sludge
14.1.2. Costing data
14.1.2.1. Investment costs
14.1.2.2. Operational costs
14.1.2.3. Annualised investment costs
14.1.3. Performance objectives
14.1.4. Applicable system configurations
14.1.5. Limitations and constraints
14.2. Optimised design procedure
14.2.1. System A1: Conventional secondary treatment
14.2.2. System A2: Secondary treatment with primary settling
14.2.3. System B1: Combined anaerobic-aerobic treatment
14.2.4. System C1: Nitrogen removal
14.2.5. System C2: Nitrogen and phosphorus removal
14.2.6. System comparison
14.3. Factors influencing design
14.3.1. Influence of the wastewater temperature
14.3.2. Influence of the sludge age
14.4. Operational optimisation
14.4.1. Comparison of different operational regimes
14.4.2. Optimised operation of existing treatment plants
14.5. Integrated design examples
14.5.1. Nutrient removal in different configurations
14.5.2. Membrane bioreactor design
- case study
14.6. Final Remarks
Reference list
Appendix 1 Determination of the oxygen uptake rate
A1.1. Determination of the apparent OUR
A1.2. Correction factors of the apparent OUR
A1.2.1. Representativeness of mixed liquor operational conditions
A1.2.2. Critical dissolved oxygen concentration
A1.2.3. Hydraulic effects
A1.2.4. Absorption of atmospheric oxygen
A1.2.5. relaxation effect
Appendix 2 Calibration of the general model
A2.1. Calibration with cyclic loading
A2.2. Calibration with batch loading
Appendix 3 non-ideal activated sludge system
Appendix 4 Determination of nitrification kinetics
Appendix 5 Determination of denitrification kinetics
Appendix 6 Extensions to the ideal model
A6.1. Imperfect solid-liquid separation in final settler
A6.1.1. Particulate organic nitrogen and phosphorus in the effluent
A6.1.2. Excess sludge production and composition
A6.2. Nitrifier fraction in the volatile sludge mass
Appendix 7 Empiric methods for final settler sizing
A7.1. Stora design guidelines (1981)
A7.1.1. Theoretical aspects
A7.1.2. Application of the STORA 1981 design guidelines
A7.1.3. Modifications to the STORA 1981 design guidelines
A7.2. Final settler design comparison methodology
A7.3. ATV design guidelines (1976)
A7.3.1. Theoretical aspects
A7.3.2. Modifications to the ATV 1976 design guidelines
Appendix 8 Denitrification in the final settler
Appendix 9 Aerobic granulated sludge
A9.1. Benefits of aerobic granular sludge systems
A9.2. System design and operation
A9.2.1. Process configurations
A9.2.2. Reactor configuration
A9.2.3. Operation of AGS systems
A9.2.4. Start-up of aerobic granular sludge reactors.