Urban Drainage
Kaup valmöguleikar
This new edition of a well-established textbook covers the health, environmental, and engineering aspects of the management of rainwater and wastewater in areas of human development. Urban Drainage deals comprehensively not only with the design of new systems but also with the analysis and upgrading of existing infrastructure. Keeping its balance of principles, practice, and research, the fifth edition has had the most comprehensive update of any edition so far.
It includes a new chapter on urban drainage planning, some significant restructuring of others and the introduction of new topics, including emerging contaminants, wastewater surveillance, AI, digital twins, and cyber-physical security. It also addresses current concerns about climate change impacts and intermittent wastewater pollution, and new ideas about sustainable and resilient systems. In all cases, the aim is to provide comprehensive, authoritative, and evidence-based content prioritising innovation, improved methods, and solutions.
This is an essential text for undergraduates and graduate students, lecturers, and researchers in water engineering, environmental engineering, public health engineering, engineering hydrology, and related non-engineering disciplines. It also serves as a dependable and up-to-date reference for drainage engineers in water service providers, local authorities, and consulting engineers. Throughout the text, extensive examples are used to support and demonstrate the key issues.
Nánar um bókina
- Taylor & Francis
- 9781040229101
- 9781032528359
- ePub
- 5
- David Butler; Christopher Digman; Christos Makropoulos; John W. Davies
- English
- 2024-12-24
- 100
- 2
- 2
Kaflar
- Cover Page
- Half Title page
- Title Page
- Copyright Page
- Contents
- Half Title
- Readership
- Acknowledgements
- Notation
- Abbreviations
- Chapter 1 Introduction
- 1.1 What is urban drainage?
- 1.2 Effects of urbanisation
- 1.3 Effects of climate change
- 1.4 Urban drainage priorities
- 1.4.1 Public health
- 1.4.2 Minimising adverse impacts
- 1.5 History
- 1.5.1 Ancient civilisations
- 1.5.2 Ancient to modern
- 1.5.3 London
- 1.6 Geography
- 1.7 Types of system
- 1.7.1 Combined systems
- 1.7.2 Separate systems
- 1.7.3 Mixed and partially separate systems
- 1.7.4 Non-pipe systems
- 1.8 Urban water system
- 1.9 Changing context
- 1.10 Future challenges
- Problems
- Key sources
- References
- Chapter 2 Water quality
- 2.1 Introduction
- 2.2 Basics
- 2.2.1 Strength
- 2.2.2 Equivalent concentrations
- 2.3 Parameters
- 2.3.1 Sampling and analysis
- 2.3.2 Solids
- 2.3.2.1 Gross solids
- 2.3.2.2 Grit
- 2.3.2.3 Suspended solids
- 2.3.2.4 Volatile solids
- 2.3.3 Oxygen
- 2.3.3.1 Dissolved oxygen
- 2.3.4 Organic compounds
- 2.3.4.1 Biochemical oxygen demand (BOD5)
- 2.3.4.2 Chemical oxygen demand (COD)
- 2.3.4.3 Total organic carbon (TOC)
- 2.3.5 Nitrogen
- 2.3.5.1 Organic nitrogen (org.N)
- 2.3.5.2 Ammonia nitrogen (NH3–N)
- 2.3.5.3 Nitrite and nitrate nitrogen (NO2−−N,NO3−−N)
- 2.3.6 Phosphorus
- 2.3.7 Sulphur
- 2.3.8 Hydrocarbons
- 2.3.9 FOG
- 2.3.10 Heavy metals and synthetic compounds
- 2.3.11 Microorganisms
- 2.3.12 Priority substances
- 2.3.12.1 Phthalates
- 2.3.12.2 PFAS
- 2.3.13 Micro- and nanoplastics
- 2.4 Processes
- 2.4.1 Hydrolysis
- 2.4.2 Aerobic degradation
- 2.4.2.1 Nitrification
- 2.4.3 Denitrification
- 2.4.4 Anaerobic degradation
- 2.5 Receiving water impacts
- 2.5.1 Emissions
- 2.5.2 Processes
- 2.5.3 Specific impacts
- 2.5.3.1 DO depletion
- 2.5.3.2 Eutrophication
- 2.5.3.3 Toxics
- 2.5.3.4 Public health
- 2.5.3.5 Aesthetics
- 2.5.4 Other causes of pollution
- 2.5.5 Scale and severity
- 2.6 Receiving water standards
- 2.6.1 Legislation and regulatory regime
- 2.6.1.1 Urban Waste Water Treatment Directive
- 2.6.1.2 Bathing Water Directive
- 2.6.1.3 Water Framework Directive
- 2.6.1.4 Marine Strategy Framework Directive
- 2.6.2 Urban Pollution Management (UPM) Manual
- 2.6.3 Environmental quality standards
- 2.6.3.1 Freshwater aquatic life standards
- 2.6.3.2 Shellfish standards
- 2.6.3.3 Bathing standards
- Problems
- Key sources
- References
- Chapter 3 Wastewater
- 3.1 Introduction
- 3.2 Domestic
- 3.2.1 Water use
- 3.2.1.1 Climate and weather
- 3.2.1.2 Demography and user behaviour
- 3.2.1.3 Socio-economic factors
- 3.2.1.4 Development type
- 3.2.1.5 Extent of and type of metering and water conservation measures
- 3.2.1.6 COVID-19 pandemic
- 3.2.1.7 Quantification
- 3.2.2 Water–wastewater relationship
- 3.2.3 Temporal variability
- 3.2.3.1 Long term
- 3.2.3.2 Annual
- 3.2.3.3 Weekly
- 3.2.3.4 Diurnal
- 3.2.4 Appliances
- 3.3 Non-domestic
- 3.3.1 Commercial
- 3.3.2 Industrial
- 3.4 Infiltration and inflow
- 3.4.1 Problems
- 3.4.2 Quantification
- 3.4.3 Exfiltration
- 3.5 Wastewater quality
- 3.5.1 Pollutant sources
- 3.5.1.1 Human excreta
- 3.5.1.2 Toilet/WC
- 3.5.1.3 Food
- 3.5.1.4 Washing, laundry, and consumer products
- 3.5.1.5 Industry
- 3.5.1.6 Carriage water and groundwater
- 3.5.2 Pollutant levels
- 3.6 Wastewater-based epidemiology
- Problems
- Key sources
- References
- Chapter 4 Rainfall
- 4.1 Introduction
- 4.2 Measurement
- 4.2.1 Rain gauges
- 4.2.1.1 Siting
- 4.2.2 Radar
- 4.2.3 Satellites
- 4.2.4 Microwave links
- 4.2.5 Other approaches
- 4.2.6 Data requirements
- 4.3 Analysis
- 4.3.1 Basics
- 4.3.2 IDF relationships
- 4.3.2.1 Definition
- 4.3.2.2 Derivation
- 4.3.2.3 IDFs in practice
- 4.3.3 Wallingford Procedure
- 4.3.4 Annual rainfall
- 4.3.5 Areal extent
- 4.3.6 Flood Estimation Handbook
- 4.3.7 Seasonality
- 4.4 Single events
- 4.4.1 Synthetic design storms
- 4.4.2 Historical single events
- 4.4.3 Critical input hyetograph (Superstorm)
- 4.5 Multiple events
- 4.5.1 Historical time series
- 4.5.2 Synthetic time series
- 4.5.2.1 Stochastic rainfall generation
- 4.5.2.2 Stochastic disaggregation models
- 4.5.2.3 Comparison of historical and synthetic series
- 4.6 Climate change
- 4.6.1 Causes
- 4.6.2 Future trends
- 4.6.3 Design rainfall under climate change
- 4.6.3.1 Design storms
- 4.6.3.2 Rainfall time series
- 4.6.4 Implications
- 4.6.5 Solutions
- Problems
- Key sources
- References
- Chapter 5 Stormwater
- 5.1 Introduction
- 5.2 Runoff generation
- 5.2.1 Initial losses
- 5.2.1.1 Interception and wetting losses
- 5.2.1.2 Depression storage
- 5.2.1.3 Representation
- 5.2.2 Continuing losses
- 5.2.2.1 Evapo-transpiration
- 5.2.2.2 Infiltration
- 5.2.2.3 Representation
- 5.2.3 Fixed (Wallingford) runoff equation
- 5.2.3.1 PIMP
- 5.2.3.2 SOIL
- 5.2.3.3 UCWI
- 5.2.3.4 Limitations
- 5.2.4 Variable (new) runoff equation
- 5.2.4.1 Impervious area runoff
- 5.2.4.2 Pervious area runoff
- 5.2.5 UK Water Industry Research (UKWIR) runoff equation
- 5.2.6 Direct runoff approach
- 5.3 Overland flow
- 5.3.1 Unit hydrographs
- 5.3.2 Synthetic unit hydrographs
- 5.3.3 Time–area diagrams
- 5.3.4 Reservoir models
- 5.3.5 Kinematic wave
- 5.4 Stormwater quality
- 5.4.1 Pollutant sources
- 5.4.1.1 Atmospheric deposition
- 5.4.1.2 Vehicles
- 5.4.1.3 Buildings and roads
- 5.4.1.4 Animals
- 5.4.1.5 De-icing
- 5.4.1.6 Urban debris
- 5.4.1.7 Spills/leaks
- 5.4.2 Surface pollutants
- 5.4.3 Pollutant levels
- 5.4.4 Representation
- 5.4.4.1 Event mean concentrations
- 5.4.4.2 Regression equations
- 5.4.4.3 Buildup
- 5.4.4.4 Washoff
- 5.5 Sewer misconnections
- Problems
- Key sources
- References
- Chapter 6 System components and layout
- 6.1 Introduction
- 6.2 Building drainage
- 6.2.1 Soil and waste drainage
- 6.2.1.1 Inside
- 6.2.1.2 Outside
- 6.2.1.3 Components
- 6.2.1.4 Layout
- 6.2.2 Roof drainage
- 6.3 System components
- 6.3.1 Sewers
- 6.3.1.1 Vertical alignment
- 6.3.1.2 Horizontal alignment
- 6.3.2 Manholes
- 6.3.3 Gully inlets
- 6.3.4 Ventilation
- 6.4 Design
- 6.4.1 Stages
- 6.4.2 Sewers for adoption
- Problems
- Key sources
- References
- Chapter 7 Hydraulics
- 7.1 Introduction
- 7.2 Basic principles
- 7.2.1 Pressure
- 7.2.2 Continuity of flow
- 7.2.3 Flow classification
- 7.2.4 Laminar and turbulent flow
- 7.2.5 Energy and head
- 7.3 Pipe flow
- 7.3.1 Head (energy) losses
- 7.3.2 Friction losses
- 7.3.3 Friction factor
- 7.3.4 Tables and charts
- 7.3.4.1 Tables
- 7.3.4.2 Charts
- 7.3.5 Roughness
- 7.3.6 Local losses
- 7.4 Part-full pipe flow
- 7.4.1 Normal depth
- 7.4.2 Geometric and hydraulic elements
- 7.4.3 Butler–Pinkerton charts
- 7.4.4 Non-circular sections
- 7.4.5 Surcharge
- 7.4.6 Velocity profiles
- 7.4.7 Minimum velocity
- 7.4.8 Minimum shear stress
- 7.4.9 Maximum velocity
- 7.5 Open-channel flow
- 7.5.1 Uniform flow
- 7.5.1.1 Manning’s equation
- 7.5.2 Nonuniform flow
- 7.5.3 Specific energy
- 7.5.4 Critical, subcritical, and supercritical flow
- 7.5.5 Gradually varied flow
- 7.5.6 Rapidly varied flow
- Problems
- Key source
- References
- Chapter 8 Hydraulic features
- 8.1 Flow controls
- 8.1.1 Orifice plate
- 8.1.2 Penstock
- 8.1.3 Vortex regulator
- 8.1.4 Throttle pipe
- 8.1.5 Flap valve
- 8.1.6 Summary of characteristics of flow control devices
- 8.2 Weirs
- 8.2.1 Transverse weirs
- 8.2.2 Side weirs
- 8.3 Sewer drops
- 8.3.1 Vortex drop shafts
- 8.3.2 Other sewer drop arrangements
- 8.4 Inverted siphons
- 8.5 Gully spacing
- 8.5.1 Road channel flow
- 8.5.2 Gully hydraulic efficiency
- 8.5.3 Gully inlet hydraulics
- 8.5.4 Spacing
- 8.5.4.1 Intermediate gullies
- 8.5.4.2 Initial gullies
- 8.5.4.3 Potential optimisation
- 8.6 Culverts
- 8.6.1 Culverts in urban drainage
- 8.6.2 Flow cases
- Problems
- References
- Chapter 9 Foul sewers
- 9.1 Introduction
- 9.1.1 Flow regime
- 9.2 Design
- 9.2.1 Choice of design period
- 9.2.2 Criterion of satisfactory service
- 9.3 Large sewers
- 9.3.1 Flow patterns
- 9.3.2 Dry weather flow
- 9.3.3 Domestic flow (PG)
- 9.3.3.1 Population (P)
- 9.3.3.2 Per capita water consumption (G)
- 9.3.4 Infiltration (I)
- 9.3.4.1 Measurement
- 9.3.4.2 Prevention
- 9.3.5 Non-domestic flows (E)
- 9.3.6 Peak flow
- 9.3.7 Design criteria
- 9.3.7.1 Capacity
- 9.3.7.2 Self-cleansing
- 9.3.7.3 Roughness
- 9.3.7.4 Minimum pipe sizes
- 9.3.8 Design method
- 9.4 Small sewers
- 9.4.1 Discharge unit method
- 9.4.1.1 Probabilistic framework
- 9.4.1.2 Design criterion
- 9.4.1.3 Mixed appliances
- 9.4.2 Design criteria
- 9.4.3 Choice of methods
- 9.5 Solids transport
- 9.5.1 Large sewers
- 9.5.2 Small sewers
- Problems
- Key sources
- References
- Chapter 10 Storm sewers
- 10.1 Introduction
- 10.1.1 Flow regime
- 10.2 Design
- 10.2.1 Design storm
- 10.2.2 Optimal design
- 10.2.3 Return period and design life probability of exceedance
- 10.3 Contributing area
- 10.3.1 Catchment area measurement
- 10.3.2 Land use
- 10.3.3 Urban creep
- 10.3.4 Runoff coefficient
- 10.3.5 Time of concentration
- 10.3.5.1 Time of entry
- 10.3.5.2 Time of flow
- 10.4 Rational Method
- 10.4.1 Steady-state runoff
- 10.4.2 Critical rainfall intensity
- 10.4.2.1 Small areas
- 10.4.3 Modified Rational Method
- 10.4.3.1 Volumetric runoff coefficient (Cv)
- 10.4.3.2 Dimensionless routing coefficient (CR)
- 10.4.4 Design criteria
- 10.4.4.1 Capacity
- 10.4.4.2 Self-cleansing
- 10.4.4.3 Roughness
- 10.4.4.4 Minimum pipe sizes
- 10.4.5 Design method
- 10.4.6 Limitations
- 10.5 Time–Area Method
- 10.5.1 The need
- 10.5.2 Diagram construction
- 10.6 Hydrograph methods
- 10.6.1 Time–Area Method
- 10.6.1.1 Limitations
- 10.6.2 Level pool routing method
- 10.6.3 Limitations
- 10.7 Undeveloped site runoff
- Problems
- Key sources
- References
- Chapter 11 Sustainable Drainage Systems (SuDS)
- 11.1 Introduction
- 11.2 Components
- 11.2.1 Inlet controls
- 11.2.1.1 Blue roofs
- 11.2.1.2 Green roofs
- 11.2.1.3 Water butts and rainwater harvesting
- 11.2.1.4 Paved area ponding
- 11.2.2 Infiltration components
- 11.2.3 Vegetated surfaces
- 11.2.4 Pervious pavements
- 11.2.5 Filter drains
- 11.2.6 Infiltration basins
- 11.2.7 Detention basins
- 11.2.8 Ponds
- 11.2.9 Constructed wetlands
- 11.2.10 Oil separators
- 11.3 Elements of design
- 11.3.1 Rainfall
- 11.3.2 Runoff
- 11.3.3 Conveyance
- 11.3.4 Inlets and outlets
- 11.3.5 Exceedance flows
- 11.3.6 Storage volume related to inflow and outflow
- 11.3.7 Infiltration from a pervious pavement sub-base
- 11.3.8 Infiltration from a soakaway or infiltration trench
- 11.3.8.1 BRE Digest 365 method
- 11.3.8.2 CIRIA 156 method
- 11.3.9 Water quality
- 11.3.9.1 Mass balance
- 11.3.9.2 Treatment volume
- 11.3.9.3 Nutrient neutrality
- 11.3.10 Amenity
- 11.3.11 Biodiversity
- 11.3.12 Multiple benefits
- 11.3.13 Modelling
- 11.4 SuDS applications
- 11.4.1 Management train
- 11.4.2 Retrofit
- 11.5 Public attitudes and community engagement
- 11.6 Issues
- 11.6.1 Long-term performance
- 11.6.2 Maintenance
- 11.6.3 Adoption
- 11.6.4 Costs
- 11.6.5 Groundwater pollution
- 11.6.6 Failures
- 11.7 Site runoff control
- 11.7.1 Design principles
- 11.7.1.1 Interception storage (small rainfall events)
- 11.7.1.2 Long-term storage (extreme rainfall events)
- 11.7.1.3 Attenuation storage (flow rate limitation)
- 11.7.1.4 Treatment volume
- 11.7.2 Non-Statutory Technical Standards (NSTS)
- 11.7.3 Statutory standards
- Problems
- Key sources
- References
- Chapter 12 Surface water flooding
- 12.1 Introduction
- 12.2 Exceedance
- 12.2.1 Systems interface
- 12.2.2 Exceedance flow
- 12.3 Standards
- 12.4 Flood risk
- 12.4.1 Flood damage
- 12.4.1.1 Flood depth
- 12.4.2 Risk assessment
- 12.4.3 Surface flood risk maps
- 12.5 Management
- 12.5.1 Options
- 12.5.2 Surface flow features
- 12.5.2.1 Gully inlets
- 12.5.2.2 Surface pathways
- 12.5.2.3 Surface storage
- 12.5.2.4 Safety
- 12.5.3 Flood protection of buildings
- 12.5.3.1 Layout
- 12.5.3.2 Fabric
- 12.6 Flood resilience
- 12.6.1 Attributes
- 12.6.2 Performance
- 12.6.3 Combined approach
- Problems
- Key sources
- References
- Chapter 13 Combined sewers and combined sewer overflows
- 13.1 Introduction
- 13.2 System flows
- 13.2.1 Low flow rates
- 13.3 The role of CSOs
- 13.3.1 Flow
- 13.3.2 Pollution
- 13.3.3 First foul flush
- 13.4 Control of pollution
- 13.4.1 CSO permits and standards
- 13.4.1.1 Technical Committee Formula A
- 13.4.1.2 Scottish Development Department (SDD)
- 13.4.1.3 Freshwater standards
- 13.4.1.4 Estuaries and coastal water standards
- 13.4.1.5 Shellfish waters standards
- 13.4.1.6 Bathing waters standards
- 13.4.1.7 Aesthetic control standards
- 13.4.2 Storm Overflows Discharge Reduction Plan
- 13.4.2.1 Protecting the environment
- 13.4.2.2 Protecting public health in designated bathing waters
- 13.4.2.3 Ensuring storm overflows operate only in unusually heavy rainfall events
- 13.4.3 Monitoring
- 13.5 CSO design
- 13.5.1 High side weir
- 13.5.1.1 Principles
- 13.5.1.2 Dimensions and layout
- 13.5.2 Screens
- 13.5.2.1 Principles
- 13.5.2.2 Development
- 13.5.2.3 Dimensions and layout
- 13.5.3 Stilling pond
- 13.5.3.1 Principles
- 13.5.3.2 Development
- 13.5.3.3 Dimensions and layout
- 13.5.4 Hydrodynamic vortex separator
- 13.5.4.1 Principles
- 13.5.4.2 Development
- 13.5.4.3 Dimensions and layout
- 13.5.5 WRcCSO
- 13.5.5.1 Principles
- 13.5.5.2 Development
- 13.5.5.3 Dimensions and layout
- 13.5.6 Storage
- 13.5.6.1 Principles
- 13.5.6.2 Development
- 13.5.6.3 Dimensions and layout
- 13.6 CSO design details
- 13.6.1 Design return period
- 13.6.2 Diameter of inflow pipe
- 13.6.3 Creating good inlet flow conditions
- 13.6.4 Weirs
- 13.6.5 Selecting, sizing and accommodating the screen
- 13.6.6 Control of outflow
- 13.6.7 Chamber invert
- 13.6.8 Top water level
- 13.6.9 Access
- 13.7 CSO performance
- 13.7.1 Pollutant removal
- 13.7.2 Choice of design
- 13.8 System management
- 13.8.1 Problems
- 13.8.2 Options
- 13.8.2.1 Treatment options
- 13.8.2.2 Sewer separation
- Problems
- Key sources
- References
- Chapter 14 Storage
- 14.1 Function of storage
- 14.2 Overall design
- 14.2.1 Online
- 14.2.2 Offline
- 14.2.3 Flow control
- 14.3 Sizing
- 14.3.1 Preliminary storage sizing
- 14.3.2 Storage routing
- 14.4 Level pool (or reservoir) routing
- 14.5 Storage routing using variation of water depth with time
- 14.6 Optimal location of storage
- Problems
- References
- Chapter 15 Pumped systems
- 15.1 Why use a pumping system?
- 15.2 General arrangement of a pumping system
- 15.3 Hydraulic design
- 15.3.1 Pump characteristics
- 15.3.2 System characteristics
- 15.3.3 Power
- 15.3.4 Pumps in parallel
- 15.3.5 Suction and delivery pipes
- 15.4 Rising mains
- 15.4.1 Differences from gravity sewers
- 15.4.1.1 Hydraulic gradient
- 15.4.1.2 Flow is not continuous
- 15.4.1.3 Power input
- 15.4.1.4 The pipes are under pressure
- 15.4.2 Design features
- 15.4.3 Surge
- 15.5 Types of pump
- 15.6 Pumping station design
- 15.6.1 Main elements
- 15.6.1.1 Wet well–dry well
- 15.6.1.2 Wet well only
- 15.6.2 Number of pumps
- 15.6.3 Control
- 15.6.4 Sump volume
- 15.6.5 Flow arrangements
- 15.6.6 Maintenance
- 15.6.7 Energy demands
- 15.7 Non-gravity systems
- 15.8 Energy use and net zero emissions
- Problems
- References
- Chapter 16 Sewer construction and rehabilitation
- 16.1 Types of construction
- 16.2 Pipes
- 16.2.1 General
- 16.2.2 Materials
- 16.2.2.1 Clay
- 16.2.2.2 Concrete
- 16.2.2.3 Ductile iron
- 16.2.2.4 Steel
- 16.2.2.5 Unplasticised PVC (PVC-U)
- 16.2.2.6 Polyethylene (PE)
- 16.2.2.7 Other materials
- 16.2.2.8 Sizes
- 16.2.3 Pipe joints
- 16.2.3.1 Spigot and socket
- 16.2.3.2 Sleeve
- 16.2.3.3 Bolted flange joints
- 16.2.3.4 Heat fusion jointing
- 16.3 Structural design
- 16.4 Site investigation
- 16.4.1 Site investigation for construction
- 16.4.2 Underground assets
- 16.5 Open-trench construction
- 16.5.1 Excavation
- 16.5.2 Pipe laying
- 16.6 Tunnelling
- 16.6.1 Lining
- 16.6.1.1 Primary lining
- 16.6.1.2 Secondary lining
- 16.6.2 Ground treatment and control of groundwater
- 16.6.2.1 Dewatering
- 16.6.2.2 Ground freezing
- 16.6.2.3 Injection of grouts or chemicals
- 16.6.2.4 Compressed air
- 16.6.3 Excavation
- 16.7 Trenchless methods
- 16.7.1 Pipejacking
- 16.7.2 Microtunnelling
- 16.7.3 Auger boring
- 16.7.4 Directional drilling (DD)
- 16.7.5 Impact moling
- 16.7.6 Pipe ramming
- 16.7.7 Timber headings
- 16.8 Rehabilitation – introduction
- 16.8.1 The need for rehabilitation
- 16.8.2 Rehabilitation approaches
- 16.9 Methods of structural renovation and repair
- 16.9.1 Renovation
- 16.9.1.1 Laterals
- 16.9.1.2 Cleaning
- 16.9.1.3 Structural aspects
- 16.9.2 Repair
- 16.10 Hydraulic rehabilitation
- Problems
- Key sources
- References
- Standards and specifications
- Chapter 17 Sediments
- 17.1 Introduction
- 17.2 Origins
- 17.2.1 Definition
- 17.2.2 Sources
- 17.3 Effects
- 17.3.1 Problems
- 17.3.2 Hydraulic
- 17.3.2.1 Suspension
- 17.3.2.2 Geometry
- 17.3.2.3 Bed roughness
- 17.3.3 Pollution
- 17.3.4 Transport
- 17.3.5 Entrainment
- 17.3.6 Transport
- 17.3.7 Deposition
- 17.3.8 Sediment beds and bed-load transport
- 17.4 Characteristics
- 17.4.1 Deposited sediment
- 17.4.1.1 Physical characteristics
- 17.4.1.2 Chemical characteristics
- 17.4.1.3 Significance of deposits
- 17.4.2 Mobile sediment
- 17.4.2.1 Suspension
- 17.4.2.2 Near-bed
- 17.4.2.3 Granular bed-load
- 17.4.2.4 Particle size
- 17.5 Self-cleansing design
- 17.5.1 Velocity based
- 17.5.2 Tractive force based
- 17.5.3 The CIRIA method
- 17.5.3.1 Self-cleansing
- 17.5.3.2 Movement criteria
- 17.5.3.3 Design procedure
- 17.5.3.4 Limitations
- Problems
- Key sources
- References
- Chapter 18 Operation and maintenance
- 18.1 Introduction
- 18.2 Maintenance strategies
- 18.2.1 Public health
- 18.2.2 Asset management
- 18.2.3 Maintain hydraulic capacity
- 18.2.4 Minimise pollution and maintain public health and safety
- 18.2.5 Minimise disruption
- 18.2.6 Reactive maintenance
- 18.2.7 Planned maintenance
- 18.2.8 Operational functions
- 18.2.9 Maintenance scheduling
- 18.3 Sewer location and inspection
- 18.3.1 Applications
- 18.3.2 Frequency
- 18.3.3 Locational survey
- 18.3.4 Manual inspection
- 18.3.5 Closed-circuit television (CCTV)
- 18.3.5.1 Propulsion
- 18.3.5.2 Camera operation
- 18.3.5.3 Manhole zoom cameras (MZCs)
- 18.3.5.4 Limitations
- 18.3.5.5 Automation
- 18.3.6 Other techniques
- 18.3.6.1 Laser profiling
- 18.3.6.2 LiDAR scanning
- 18.3.6.3 Sonar
- 18.3.6.4 Infrared
- 18.3.6.5 Acoustics
- 18.3.6.6 UAVs
- 18.3.7 Data storage and management
- 18.4 Sewer monitoring
- 18.4.1 Flow surveys
- 18.4.2 CSO monitors
- 18.4.3 Smart manholes
- 18.5 Sewer blockage
- 18.5.1 Definition
- 18.5.2 Causes
- 18.5.2.1 Gross solids/sanitary waste (input)
- 18.5.2.2 FOG/scale (input)
- 18.5.2.3 Sediment (input)
- 18.5.2.4 Defects (system)
- 18.5.2.5 Traps (system)
- 18.5.2.6 Intruding laterals (system)
- 18.5.2.7 Tree roots (system)
- 18.5.3 Prediction and detection
- 18.5.4 Blockage control
- 18.5.4.1 Flushability standards
- 18.5.4.2 Customer awareness campaigns
- 18.5.4.3 Operational techniques
- 18.6 Sewer cleaning
- 18.6.1 Objectives
- 18.6.2 Cleaning techniques
- 18.6.2.1 Rodding or boring
- 18.6.2.2 Winching or dragging
- 18.6.2.3 Jetting
- 18.6.2.4 Flushing
- 18.6.2.5 Hand excavation
- 18.6.2.6 Invert traps
- 18.6.2.7 Gully pots
- 18.6.3 Comparison of methods
- 18.6.4 FOG control
- 18.6.4.1 At source
- 18.6.4.2 Recycling
- 18.6.4.3 Chemical treatment
- 18.6.4.4 Bio-augmentation
- 18.7 Ancillary and network equipment maintenance
- 18.8 SuDS maintenance
- 18.9 Health and safety
- 18.9.1 Atmospheric hazards
- 18.9.2 Physical injury
- 18.9.3 Infectious diseases
- 18.9.4 Safety equipment
- 18.9.5 Rodent control
- 18.10 Gas generation and control
- 18.10.1 Mechanisms
- 18.10.2 Favourable conditions
- 18.10.3 Sulphide buildup
- 18.10.4 H2S control
- 18.10.4.1 Sewerage detail design
- 18.10.4.2 Ventilation
- 18.10.4.3 Aeration
- 18.10.4.4 Oxidation
- 18.10.4.5 Chemical addition
- 18.10.5 Greenhouse gases
- Problems
- Key sources
- References
- Chapter 19 Planning
- 19.1 What is drainage planning?
- 19.1.1 Need and development
- 19.1.2 Frameworks in practice
- 19.1.3 Wider asset management
- 19.2 Creating drainage plans
- 19.2.1 Elements that steer drainage plans
- 19.2.1.1 Cost
- 19.2.1.2 Carbon
- 19.2.1.3 Benefits
- 19.2.1.4 Level of service and risk management
- 19.2.1.5 Legal and regulatory requirements
- 19.2.1.6 Investment choices within a Totex framework
- 19.2.1.7 Maximising existing asset life and value
- 19.2.1.8 Responding to public pressure
- 19.2.2 Understanding asset performance
- 19.2.2.1 Current and future performance quantification
- 19.2.2.2 Critical factors
- 19.2.3 Evaluating costs, carbon and benefits of plans, programmes and projects
- 19.2.3.1 Determining costs
- 19.2.3.2 Determining carbon emissions
- 19.2.3.3 Determining benefits
- 19.2.3.4 Utilising a cost–carbon–benefit framework
- 19.2.4 Engaging with stakeholders
- 19.3 Drainage planning in the broader context
- 19.3.1 Applying systems thinking
- 19.3.2 Integrated planning
- 19.3.3 Creating adaptive plans to align investment choices through collaboration
- 19.3.3.1 Connecting opportunities from different organisations
- 19.3.3.2 Creating aligned plans in the future
- Problems
- Key sources
- References
- Chapter 20 Modelling in practice
- 20.1 Models in urban drainage engineering
- 20.1.1 Use of models
- 20.1.2 Model types
- 20.1.3 Modelling aims
- 20.2 Urban drainage models in context
- 20.2.1 The modeller
- 20.2.2 Confidence in the model
- 20.2.3 Model use
- 20.3 Elements of urban drainage models
- 20.3.1 Overview of the components
- 20.3.2 Rainfall
- 20.3.3 Rainfall to runoff
- 20.3.4 Overland flow direct from runoff
- 20.3.5 Dry weather flow
- 20.3.6 Infiltration
- 20.3.7 Surface flooding
- 20.4 Water quality modelling
- 20.4.1 The processes to be modelled
- 20.4.2 Wastewater inflow
- 20.4.3 Catchment surface
- 20.4.4 Gully pots
- 20.4.5 Transport through the system
- 20.4.6 Pipe and tank deposits
- 20.5 Matching the modelling approach to the aims
- 20.6 Setting up and validating a system model
- 20.6.1 Input data
- 20.6.2 Model testing
- 20.6.3 Flow surveys
- 20.6.4 Model calibration/verification against measured flow data
- 20.6.5 Evaluating confidence
- 20.6.6 Documentation
- 20.7 Using water quality models
- 20.7.1 Model applications
- 20.7.2 Types of sewer quality models
- 20.7.3 Types and complexity of river quality models
- 20.7.4 Planning an integrated quality study
- 20.7.4.1 Drivers
- 20.7.4.2 Catchment boundary
- 20.7.4.3 Waterbodies
- 20.7.4.4 River modelling approach
- 20.7.4.5 Point source discharges
- 20.7.4.6 Rainfall and evaporation
- 20.7.5 Input data and model calibration/verification
- 20.7.6 Data collection in sewers and receiving waters
- 20.8 Modelling flow in sewers
- 20.8.1 Representing unsteady flow
- 20.8.2 The Saint-Venant equations
- 20.8.3 Simplifications of the full equations
- 20.8.4 Numerical methods of solution
- 20.8.5 Surcharge
- 20.9 Modelling SuDS
- 20.10 Modelling flooding
- 20.10.1 DTM/DEMs
- 20.10.2 Virtual flood cones
- 20.10.3 One-dimensional–two-dimensional (1D–2D) coupled models
- 20.10.4 Rapid flood spreading models
- 20.11 Modelling quality
- 20.11.1 Advection/dispersion
- 20.11.2 Completely mixed “tank”
- 20.11.3 Sediment transport
- 20.11.3.1 Mechanics
- 20.11.3.2 Sediment bed
- 20.11.3.3 Solid attachment
- 20.11.4 Gross solids
- 20.11.5 Modelling pollutant transformation
- 20.11.6 Conservative pollutants
- 20.11.7 Simple decay expressions
- 20.11.8 Complex processes approach
- 20.11.8.1 Oxygen balance
- 20.11.8.2 Reaeration
- 20.11.8.3 Oxygen consumption in the bulk flow
- 20.11.8.4 Oxygen consumption in the biofilm
- 20.11.8.5 Oxygen consumption in the sediment
- Problems
- Key sources
- References
- Chapter 21 Innovations in modelling
- 21.1 Introduction
- 21.2 Alternative, non-physically based, modelling approaches
- 21.2.1 Empirical models
- 21.2.2 Machine Learning Models and AI
- 21.2.3 Conceptual or meta-models
- 21.2.4 Stochastic models
- 21.3 Optimisation
- 21.4 Integrated modelling
- 21.4.1 Why do we need integrated models?
- 21.4.2 Defining and classifying the level of integration
- 21.4.3 Methods and tools for integrated system modelling and design
- 21.4.4 Benchmarks
- 21.5 Coupling model to other models: Emerging standards
- 21.6 Calibration aspects for integrated urban wastewater systems
- 21.6.1 Computational approaches
- 21.7 Uncertainty analysis
- 21.7.1 Types of uncertainty in urban drainage modelling
- 21.7.2 Uncertainty analysis in urban drainage modelling
- 21.8 Virtual case studies
- 21.9 Visualising the results of models
- 21.9.1 Emerging trends in visualisation: immersive and playful
- Problems
- Key sources
- References
- Chapter 22 Smart systems
- 22.1 Introduction
- 22.2 New data sources
- 22.2.1 Earth observation and soft sensors
- 22.2.2 Crowdsourcing and citizen observatories
- 22.3 Digital twins
- 22.4 Real-time control
- 22.4.1 Definition
- 22.4.2 Equipment
- 22.4.2.1 Sensors
- 22.4.2.2 Regulators
- 22.4.2.3 Controllers
- 22.4.2.4 Data transmission systems
- 22.4.3 Control
- 22.4.3.1 Classification
- 22.4.3.2 Control loop
- 22.4.3.3 Control strategy
- 22.4.4 Integrated control
- 22.4.4.1 Multi-objective control
- 22.4.4.2 Emerging approaches
- 22.4.5 Applicability
- 22.4.6 Benefits and drawbacks
- 22.5 Early warning systems
- 22.5.1 Definition and elements
- 22.5.1.1 Risk knowledge
- 22.5.1.2 Monitoring and warning service
- 22.5.1.3 Dissemination
- 22.5.1.4 Emergency response capacity
- 22.5.2 Forecast services
- 22.5.2.1 Flow forecasting models
- 22.5.2.2 Meteorological predictions
- 22.5.2.3 Flood occurrence criteria
- 22.6 Emerging risks in cyber-physical urban water systems
- Problems
- Key sources
- References
- Chapter 23 Low-income communities
- 23.1 Introduction
- 23.2 Public health implications
- 23.2.1 Diseases
- 23.2.2 Concerns
- 23.3 Option selection
- 23.3.1 Sanitation
- 23.3.2 Storm drainage
- 23.4 On-site sanitation
- 23.4.1 Latrines
- 23.4.1.1 Pit latrine
- 23.4.1.2 VIP latrines
- 23.4.1.3 Pour-flush latrines
- 23.4.1.4 Composting latrines
- 23.4.1.5 Communal latrines
- 23.4.2 Septic tank systems
- 23.4.3 Aqua privies
- 23.4.4 Urine-diverting dry toilets
- 23.4.5 New technologies
- 23.5 Off-site sanitation
- 23.5.1 Bucket latrines
- 23.5.2 Vault latrines
- 23.5.3 Conventional sewerage
- 23.5.3.1 Septicity
- 23.5.3.2 Blockage
- 23.5.4 Unconventional sewerage
- 23.5.4.1 Simplified sewerage
- 23.5.4.2 Settled sewerage
- 23.6 Storm drainage
- 23.6.1 Flooding
- 23.6.2 Open drainage
- 23.6.2.1 Open channels
- 23.6.2.2 Road-as-drain
- 23.6.3 Closed drainage
- 23.6.3.1 Conventional drainage
- 23.6.3.2 Dual drainage
- 23.6.4 SuDS
- 23.7 Grey water management
- 23.7.1 Options
- 23.8 Impact of climate change
- Problems
- Key sources
- References
- Chapter 24 Towards sustainable and resilient urban water management
- 24.1 Introduction
- 24.2 Sustainability: definitions and objectives
- 24.2.1 Sustainable development
- 24.2.2 Sustainability
- 24.2.3 Sustainable urban water management
- 24.2.4 Sustainability in urban drainage
- 24.2.5 Sustainability and climate change
- 24.3 Building sustainability in urban drainage
- 24.3.1 Strategies
- 24.3.2 Water transport
- 24.3.2.1 Downstream performance
- 24.3.2.2 User acceptance
- 24.3.2.3 Water and energy consumption
- 24.3.3 Mixing of industrial and domestic wastes
- 24.3.4 Mixing of stormwater and wastewater
- 24.3.5 Integration
- 24.3.6 Decentralisation – does size matter?
- 24.3.7 Hybrid grey–green systems
- 24.4 Promising technologies and approaches
- 24.4.1 Grey water recycling
- 24.4.2 Nutrient recycling
- 24.4.3 Heat recovery
- 24.5 Assessing sustainability
- 24.6 Resilience: definitions and objectives
- 24.6.1 Threats
- 24.6.2 Interpretations and applications
- 24.6.3 Resilience and sustainability
- 24.7 Building resilience in urban drainage
- 24.7.1 Strategies
- 24.7.2 Attributes and interventions
- 24.8 Assessing resilience
- 24.8.1 Resilience in strategic planning
- 24.8.2 Developing approaches
- 24.9 Where to next?
- 24.9.1 Urban futures
- 24.9.2 Transition states
- 24.9.3 Pathways
- Problems
- Key sources
- References
- Index