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Drinking Water Treatment Overview Filtration and Disinfection

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Title: Drinking Water Treatment Overview Filtration and Disinfection


1
Drinking Water Treatment OverviewFiltration and
Disinfection
  • April 16th, 2009
  • Yousry Hamdy, M.Sc., P.Eng
  • Nicolás Peleato, EIT

2
Table of Contents
  • Introduction
  • Filtration
  • Cartridge filters
  • Chemical assisted filtration
  • Slow sand filters
  • Diatomaceous earth
  • Activated carbon
  • Membrane filters
  • Disinfection
  • Chlorine
  • Chloramines
  • Ultraviolet Radiation

3
IntroductionPurpose of Treatment
  • The objective is to provide safe drinking water
    to consumers that meet the Provincial Drinking
    Water Quality Standards (O.Reg. 169/03)
  • Treatment of source water is aimed at
  • Achieving (O.Reg 170)
  • 4 log removal for viruses,
  • 3 log removal for Giardia lamblia,
  • 2 log removal of Cryptosporidium
  • Reduction of harmful chemical compounds to meet
    the Standards

4
IntroductionTreatment Elements
  • Treatment can generally be broken up into three
    aspects
  • Filtration
  • Physically removes contaminants, physical
    impurities, micro-organisms
  • Primary Disinfection
  • Inactivates micro-organisms
  • Secondary Disinfection
  • Ensures continual disinfection and prevents the
    re-growth of micro-organisms during distribution

5
FiltrationCartridge Filters
Crypt. Credit 2-log Giardia Credit 2-log Virus
Credit 0
  • Small in-line filters which physically block
    particulates and contaminants
  • Typical 5 micron pore size (can be less)
  • Can be constructed from several materials,
  • Ceramics
  • Wool, paper, woven fibers
  • Carbon
  • Depending on the filter material they are either
    disposable or can be washed and reused

6
FiltrationCartridge Filters
Crypt. Credit 2-log Giardia Credit 2-log Virus
Credit 0
  • Some also contain ion exchange resins for
    reduction of aqueous ions (iron, lead, copper,
    etc.)

Cartridge
Housing
7
FiltrationCartridge Filters
Crypt. Credit 2-log Giardia Credit 2
log Virus Credit 0
  • To claim removal credits,
  • Raw water must have turbidity less than 5 NTU,
    colour less than 5 TCU
  • Use filter elements and housing certified for
    surrogate particle removal evaluation in
    accordance with testing procedures and
    manufacturing quality control specified in
    ANSI/NSF Standard 53 or equivalent

8
FiltrationCartridge Filters
Crypt. Credit 2-log Giardia Credit 2
log Virus Credit 0
  • To claim removal credits (contd),
  • Ensure that differential pressures across the
    filter medium do not exceed manufacturers rating
    and materials coming in contact with water
    conform to ANSI/NSF Standard 61.
  • Turbidity of treated water should be at least
    monitored daily (continuous recommended)
  • Monitoring results should indicate turbidity less
    than 0.2 NTU for 95 of measurements in a month

8
9
FiltrationCartridge Filters
Crypt. Credit 2-log Giardia Credit 2
log Virus Credit 0
  • Advantages
  • Easy to operate and maintain
  • Issues
  • Only suitable for low turbidity sources
  • Cartridges can foul quickly and need to be
    replaced

10
FiltrationChemical Assisted
Crypt. Credit 2.0-log Giardia Credit
2.5-log Virus Credit 2.0-log
  • The physical filtration process is preceded by
    flocculation/coagulation where a chemical allows
    for suspended particles to aggregate and form a
    larger particle
  • Process is initiated by the addition of a
    flocculant,
  • Aluminum sulfate (Alum)
  • Ferric sulfate
  • Various polymers
  • Others

11
FiltrationChemical Assisted
Crypt. Credit 2.0-log Giardia Credit
2.5-log Virus Credit 2.0-log
  • Four steps to the process
  • Charges on suspended particles are neutralized to
    allow them to aggregate
  • Rapid mixing to eliminate concentration gradients

Coagulation
Sedimentation
Filtration
Flocculation
Untreated Water
Addition of flocculant/coagulant
  • Particles aggregate into flocs (aided by the
    chemical)
  • Gentle mixing as to promote floc growth without
    breaking them
  • Flocs are allowed to settle by gravity. The
    process can be sped up by using inclined settling
    plates.
  • Water is then typically passed through sand bed
    filters to remove any remaining flocs and
    provides further filtration
  • Filtration process is generally considered rapid,
    gt 4 m/h velocity

12
FiltrationChemical Assisted
Crypt. Credit 2.0-log Giardia Credit
2.5-log Virus Credit 2.0-log
  • Advantages
  • Highly effective filtration process
  • Flow rate through filters is high
  • Disadvantages
  • High operational duty between adjusting the
    flocculation/coagulation processes and filter
    backwash
  • Large equipment footprint

13
FiltrationChemical Assisted
Crypt. Credit 2.0-log Giardia Credit
2.5-log Virus Credit 2.0-log
  • To be effective,
  • Chemical coagulant/flocculant has to be used at
    all times and dosage must be adjusted in response
    to raw water quality fluctuations
  • Sand filters must be backwashed regularly
  • Filtrate turbidity must be continuously monitored
  • Filtered water should be less than 0.3 NTU for
    95 of the measurements each month

14
FiltrationDirect Filtration
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 1.0-log
  • The sedimentation step of chemically assisted
    filtration can be skipped and is then considered
    direct filtration
  • Only used when turbidity is less than 20 NTU
  • Must meet criteria for chemical assisted
    filtration to claim credits.

15
FiltrationDirect Filtration
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 1.0-log
  • Advantages
  • Effective filtration process
  • Flow rate through filters is reasonably high
  • Need for a sedimentation tank (or time) is
    eliminated
  • Disadvantages
  • High operational duty between adjusting the
    flocculation/coagulation processes and filter
    backwash
  • Only suitable for low turbidity waters which are
    seasonally consistent

16
FiltrationSlow Sand
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 2.0-log
  • The slow sand filtration is both a physical and
    biological process
  • Slow sand filters differ from rapid sand filters,
  • Velocities of 0.1 0.4 m/s
  • Microbial growth is promoted at the top of the
    filter
  • Backwashing procedures cannot be carried out
  • Cleaning is typically performed by removing and
    discarding the top layer of sand
  • Several weeks are needed to allow for the
    microbial layer to form (before filter can be
    used)

17
FiltrationSlow Sand
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 2.0-log
  • To be effective,
  • An active biological layer must be maintained
  • The filter must be cleaned regularly
  • Filtrate turbidity must be monitored
  • Filtered water should be less than 1 NTU for 95
    of the measurements in a month

18
FiltrationSlow Sand
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 2.0-log
  • Advantages
  • Low cost
  • Simple operation, reliable
  • Does not require extensive control
  • Issues
  • Not suitable for high turbidity waters
  • Filter surface needs regular maintenance
  • Large equipment footprint due to low flow rate

19
FiltrationDiatomaceous Earth
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 1.0-log
  • Skeletal remains of small single celled organisms
    (diatoms)
  • Used as filter media
  • A thin layer of DE is formed on a septum and
    water is passed through
  • DE is well suited for small systems because,
  • Low cost
  • Chemical coagulation/flocculation is not needed

20
FiltrationDiatomaceous Earth
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 1.0-log
21
FiltrationDiatomaceous Earth
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 1.0-log
  • To be effective,
  • A minimum thickness of the pre-coat must be
    maintained (32mm)
  • Discharge or recycle water involved in the
    pre-coat process
  • Continuously monitor filtrate turbidity
  • Filtered water must be less than 1.0 NTU for 95
    of the measurements in a month

22
FiltrationDiatomaceous Earth
Crypt. Credit 2.0-log Giardia Credit
2.0-log Virus Credit 1.0-log
  • Advantages
  • Effective filtration process
  • Simple to operate
  • Low initial capital cost
  • Issues
  • Only suitable for source waters of low turbidity
    and bacterial counts (turbidity lt 20 NTU)
  • Potentially difficult to maintain pre-coat

23
FiltrationMembrane Filtration
Crypt. Credit 3.0-log Giardia Credit - Virus
Credit 2-3 log
  • Involves passing water through a thin synthetic
    semi-permeable membrane
  • Many different types generally categorized by
    their selectivity (size of retained particles)
  • Micro-filtration gt 100 nm
  • Ultra-filtration gt 10 nm
  • Nano-filtration gt 1 nm
  • Reverse Osmosis lt 1 nm
  • Can require high pressures to achieve reasonable
    flow rates (depends on type of membrane)

24
FiltrationMembrane Filtration
Crypt. Credit 3.0-log Giardia Credit - Virus
Credit 2-3 log
  • Removal capability depend on the manufacturer and
    type of membrane (must be certified)
  • To be effective,
  • The membrane must be backwashed or cleaned
    regularly
  • Monitor membrane integrity (through particle
    count, pressure decay measurements, etc.)
  • Continuously monitor filtrate turbidity
  • Filtered water must be less than 0.1 NTU (99 of
    the time)

25
FiltrationMembrane Filtration
Crypt. Credit 3.0-log Giardia Credit - Virus
Credit 2-3 log
  • Advantages
  • Small equipment footprint
  • Automated operation
  • Issues
  • Membrane fouling can be a significant problem
    depending on the quality of source water

26
FiltrationActivated Carbon
Crypt. Credit - Giardia Credit - Virus
Credit -
  • A type of filter media that can be used
    (partially or fully) in bed filters, cartridge
    filters, or as a powder
  • Processed carbon which results in a structure
    with very high surface area
  • 1 g of activated carbon has a surface area of
    apprx. 500 m2
  • Adsorbs particulates, metal ions, micro-organisms
  • Must be recharged or replaced periodically

27
FiltrationActivated Carbon
Crypt. Credit - Giardia Credit - Virus
Credit -
  • Sometimes added in powdered format (PAC) during
    seasonal taste and odour events.
  • PAC adsorbs contaminants and can then be filtered

28
FiltrationActivated Carbon
Crypt. Credit - Giardia Credit - Virus
Credit -
  • Advantages
  • Powerful non-selective adsorbent
  • Can be recycled and reused
  • Issues
  • Must be recharged periodically
  • More expensive than typical medias

29
Summary
30
Disinfection Chlorine
  • Most common method of disinfecting water
  • Can be applied by using,
  • Chlorine gas
  • Sodium hypochlorite
  • Calcium hypochlorite
  • Electrochemical process
  • Disinfection is caused by free chlorine

31
Disinfection Chlorine
  • Inactivates a broad range of pathogens through
    oxidation
  • Can be considered both a primary and secondary
    disinfectant since free chlorine persists for
    extended periods of time
  • The extent of disinfection is determined by the
    concentration of residual chlorine and the amount
    of time it is in contact with the water.
  • Contact chambers are used to increase contact
    time
  • Log credits calculated through the CT
    disinfection concept

32
Disinfection Chlorine
  • CT disinfection concept
  • CT concentration (mg/L) x contact time
    (minutes)
  • Disinfectant residual concentration is measured
    at the end of a treatment step
  • CT requirement table example (virus inactivation)

33
Disinfection Chlorine
  • Chlorine is effective at removing almost all
    pathogens and providing secondary disinfection
  • Chlorine (gas)
  • Cheapest based on available chlorine
  • Very dangerous gas and must be handled with care
  • Sodium hypochlorite (liquid solution)
  • More expensive
  • Easier to handle than gas (but still corrosive)

34
Disinfection Chlorine
  • Calcium hypochlorite (solid)
  • Very stable and can be stored for a year or more
  • Corrosive
  • Reaction between calcium hypochlorite and organic
    materials can generate enough heat to start a
    fire
  • Readily absorbs moisture and releases chlorine
    gas

35
Disinfection Chloramination
  • Combination of chlorine and ammonia
  • Can form several species of chloramines however
    monochloramine is desirable
  • Promoted using mass ratio of 4.51
    (chlorineammonia)
  • Not suitable for primary disinfection
  • More persistent and less reactive than free
    chlorine,
  • Better for large distribution systems
  • Reduces number of disinfection by-products formed
    in distribution system

36
Disinfection Chloramination
  • Advantages
  • Results in fewer DBPs formed in distribution
    system
  • More persistent residual (good for distribution
    systems with high retention times)
  • Issues
  • Weak disinfectant
  • Disagreeable taste and odour

37
Disinfection Ultraviolet Radiation
  • Application of UV radiation provides primary
    disinfection by inactivating the reproductive
    abilities of micro-organisms
  • Provides no residual (no secondary disinfectant)
  • Disinfection depends on the intensity of the
    radiation, transmittance, and contact time
  • Dose is calculated at a wavelength of 254nm
  • Minimum of 40 mJ/cm2 (flux)

38
Disinfection Ultraviolet Radiation
  • UV systems must be certified by the NSF, EPA, or
    equivalent organizations
  • Systems must have an alarm and auto-shut off
    feature
  • If dose falls below set-point
  • If turbidity exceeds manufacturer standards
    causing low transmittance of UV

39
Disinfection Ultraviolet Radiation
39
40
Disinfection Ultraviolet Radiation
  • Advantages
  • Produces no known toxic residuals
  • Requires very short contact times
  • Easy to operate and maintain
  • UV lamps only need to be replaced every one or
    two years
  • Effective disinfectant
  • Issues
  • Source water must have high transmittance at 254
    nm
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