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Mechanical Filtration

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Mechanical Filtration Hugh S. Hammer, PhD GSCC Ron Malone, PhD LSU Joe Fox, PhD Texas A&M * Over-Drain Flow Captured Solids Microscreen Cleaning Jets Granular Media ... – PowerPoint PPT presentation

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Title: Mechanical Filtration


1
Mechanical Filtration
  • Hugh S. Hammer, PhD GSCC
  • Ron Malone, PhD LSU
  • Joe Fox, PhD Texas AM

2
Total Solids
  • The amount of solid material left in a container
    after the water has evaporated.
  • Total Solids Total Suspended Solids (TSS)
    Total Dissolved Solids (TDS)
  • Total Suspended Solids (TSS) are solids that can
    be trapped by a filter. Examples silt, decaying
    organic material, industrial wastes, sewage
  • Total Dissolved Solids (TDS) are solids that pass
    through a filter (0.45 microns). Examples
    carbonates, bicarbonate, chloride, sulfate,
    phosphate, nitrate, calcium, magnesium, sodium
    and other ions.
  • TOTAL SOLIDS ARE INDICATORS OF POLLUTION

3
Sources of Total Suspended Solids
  • High flow rates from fast moving water, silt,
    sand, clay, organics
  • Soil erosion (non-point source)
  • Urban runoff (non-point source)
  • Waste water and septic effluent
  • Decaying organic matter
  • Fish that stir up sediments (carps)

4
Problems with TSS
  • Increased biotic and abiotic turbidity
  • Reduced light transmittance and photosynthesis
  • Unstable dissolved oxygen
  • Increase water temperature
  • Abiotic sources can clog gills and increase
    disease
  • Smother eggs, filter feeding animals, and aquatic
    insects
  • High TSS is often an indicator of other types of
    pollutants and toxins (mercury and PCB)

5
Testing TSS
  • A water sample is filtered through a pre-weighed
    filter (0.45 microns)
  • The residue retained in the filter is dried in an
    oven at 103 to 105 C
  • The sample is dried to constant weight and the
    weight is recorded
  • Reported as grams per liter (ppt)

6
Total Dissolved Solids
  • The water sample is passed through a 0.45 micron
    filter
  • The water that passes through the filter is dried
    in a pre-weighed dish at 180 C
  • The sample is dried to constant weight
  • TDS is reported as milligrams per liter (ppm)
  • This is directly related to the conductance of
    water (dissolved ions)
  • EPA standard of 500 ppm for drinking water

7
Sources of TDS
  • Geology and sediment composition
  • Fertilizer run-off
  • Waste-water and septic effluent
  • Soil erosion
  • Urban run-off
  • The TDS frequently includes phosphorous,
    nitrate, and other nutrients

8
Aquaculture Solids
Solids
FEED
FECES
Uneaten Feed
9
Mechanical Filtration
  • Solids removal employs systems from the
    wastewater treatment industry
  • Screening, gravity separation (sedimentation,
    centrifuging, hydrocycloning) or adsorption
    between particulate beds
  • Processes designations for RAS
  • Primary one or more gravity methods
  • Secondary biological filtration
  • Tertiary ion exchange, reverse osmosis, foam
    fractionation, carbon adsorption, sometimes
    disinfection

10
Solids Characterization
  • Three means of classification
  • Solid materials are further classified as being
    either settleable, suspended, dissolved or
    colloidal
  • Difference between settleable and suspended
    solids is a matter of practicality
  • Most settleable gt 10 µM (settle in an Imhoff
    cone in less than 1 hr)
  • Particles passing through a 1.2 µM membrane
    filter are dissolved, suspended are trapped
  • Dissolved particles consist of some organic and
    inorganic ions and molecules present in solution

11
Particle Size Distribution (microns)
Settleable
10-4 10-3 10-2
10-1 1 10
100
Dissolved
Colloidal
Suspended
12
SOLIDS REMOVAL PROCESSES AND PARTICLE SIZES
13
Impact of Solids on Recirculating Systems
  • Increased BOD causes oxygen availability
    problems with animals and biofilters
  • Organic wastes (feces) build up increasing
    ammonia and nitrite levels (toxic)
  • Increased system turbidity, decreased water
    clarity (fine particles)
  • Gill damage in fish (fine particles) can create
    opportunities for diseases

14
Waste Solids Become Chemical Problems
  • Both uneaten feed and fecal material become toxic
    ammonia through the action of decomposing
    bacteria.

Uneaten Feed
Feces
Heterotrophic Bacteria
Ammonia NH3/NH4
15
Increased Biochemical Oxygen Demand (BOD)
Oxygen
Oxygen
Oxygen
Heterotrophic Bacteria
Oxygen
Oxygen
Oxygen
16
Tilapia
No Fine Solids Capture
17
Tiger Barbs
18
Settleable Solids Removal
  • If screens arent used, wastewater is first
    treated by simple sedimentation (primary
    treatment)
  • Separation is via gravity settling
  • As with ponds, the principle design criteria are
    the basins cross-sectional area, detention time,
    depth and overflow rate (refer to previous notes)
  • Ideal sedimentation basins dont exist in the
    real world due to a variety of particle sizes,
    composition, etc.
  • Once settling velocity is known, basic dimensions
    can be estimated

19
Sedimentation
  • Advantages
  • Inexpensive
  • Works by gravity and doesnt require energy
  • Disadvantages
  • Only gets largest solids
  • Takes a lot of space
  • Labor intensive to clean

20
SEDIMENTATION
Vh
OUTFLOW
Vs
Settling Zone
INFLOW
Inlet Zone
Outlet Zone
(Vs gt Overflow Rate to settle)
Sludge Zone
21
Sedimentation Tanks and Basins
22
Sedimentation Tank
23
Plate and Tube Separators
  • Also work on principle of gravity
  • Actually enhance settling capacity of basins
  • Typically shallow settling devices consisting of
    modules of flat parallel plates or inclined tubes
    of various geometric design
  • Used in primary thru tertiary treatment
  • Limited success

24
Centrifuges and cyclonic separators
  • Increase gravitational force on particles via
    spinning motion (i.e., settling rate increases)
  • Many devices rated at different g forces
  • Work best on freshwater systems due to many
    particles having similar densities to that of
    seawater
  • Most practical are hydrocyclones or cyclonic
    separators
  • Heavy particles are moved by higher outside
    velocity to outside and downward
  • Underflow exiting unit is very small and high
    density, cleaner water exits top

25
Under-gravel Filters
  • Advantages
  • Easy to build and operate
  • Inexpensive
  • Does both mechanical and biological filtration
  • Disadvantages
  • Needs to be vacuumed regularly (lots of
    maintenance)
  • Clog easily
  • Cant handle big loads (mainly for aquariums and
    not practical for aquaculture production)

26
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27
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28
Airlifts Perform Several Functions
  • Circulation
  • Aeration
  • C02 stripping
  • Foam control

29
Circulation Options
Circulation
Pump
30
Screens
  • Simplest, oldest method, pre-treatment prior to
    primary treatment
  • Placed across flow path of RAS water
  • Coarse screens handle raw effluent, biofloc fine
    screens for tertiary treatment
  • Many materials fibers to A/C filters cost
    increases with decreased mesh size
  • Static vs. rotary screens (0.25 to 1.5 mm about
    4-16 gpm flow per square inch of screen removal
    efficiency around 5-25
  • Rotary screens for fine solids removal are 50-70
    efficient 15-60 µM

31
Screens
  • Disadvantages
  • May be difficult to remove and clean
  • Labor intensive to clean
  • Auto wash micro-screen filters use a lot of water
  • Some Units very expensive (10,000)
  • Get mainly large solids and clog quickly
  • Advantages
  • Simple concept
  • Can be inexpensive and simple to build (socks,
    panti-hose, furnace filters, mesh bags)

32
Micro-screen Filters
33
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34
Over-Drain Flow
35
Captured Solids
36
Microscreen Cleaning Jets
37
Granular Media Filters
  • Commonly referred to as sand or bead filters
  • Two types slow and rapid filters
  • Advantages
  • Less labor is required (typically only to
    backwash)
  • Gets a wide variety of solid sizes (down to 20
    microns)
  • Require less water than some units
  • Mechanical and Biological filters (depending on
    the media)
  • Best all-around mechanical filters
  • Capable of handling large loads (production
    aquaculture)
  • Disadvantages
  • Requires a lot of pressure for some (pumps)
  • Expensive
  • Can be more complex to operate
  • Can clog quickly depending on the media

38
Slow Sand Filters
  • Usually custom-built, open to atm
  • Loading rates are slow, 0.6-0.7 lps/m2
  • Particle size 30 µM max
  • For this reason require more floor space
  • Used in gravity flow situations
  • Downside cleaning

39
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40
Rapid Sand Filters
  • Typically closed, pressurized units
  • Handle high flow rates 20 gpm/ft2
  • Downside very high head loss (30-90 ft)
  • Only really good for low solids process streams
    with some sort of pre-trt
  • Backwashing can be made automatic

41
Granular Filters
42
Important Point
  • Sand filters can be used in series to filter out
    different size particles so that they dont clog
    quickly.
  • Large gravel Small gravel sand filter
  • This is frequently used for facilities that bring
    in natural water (such as seawater)

43
BEAD FILTERS
(a) Propeller-washed
(b) Bubble-washed
44
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45
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46
Propeller-washed Floating Bead Filters
47
Broodstock
Return
Anti-siphon valve
Bypass
Sludge View Port
Pressure Gauge
Sludge
Intake
48
ADM System Prop-Washed Bead Filters
Motor and Backwash Propeller
Pump
49
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50
Filter Mode
Drop Filters Low Water Loss Floating Bead
Bioclarifiers
Air Bleed Builds Charge
Settled Backwash Waters returned to system
51
Backwash mode
Drop Filters Low Water Loss Floating Bead
Bioclarifiers
Released Air Washes Beads
Internal Sludge Capture
52
Circulation Aeration Degassing
Solids Capture Biofiltration
Inlet
Airlift
53
Cartridge Filters
  • Consist of cannister and replaceable cartridge
  • Advantages
  • Removes very small particles
  • Max particle retention is 0.01 µM (0.00001 mm)
  • Very high water clarity
  • Great for aquariums
  • Disadvantages
  • Can be expensive
  • Can clog quickly
  • Cant handle large volumes
  • Not practical for production aquaculture

54
Sock and Canister Filters
55
Diatomaceous Earth (DE) Filters
  • Granular material composed of diatom skeletons
    (frustules)
  • Can serve as replacement for cartridge filters,
    but require pre-filtration
  • Fine grade DE can filter down to 0.1 µM

56
Factors to Consider
  • Particle size to be removed
  • Amount of energy required to operate
  • Labor and maintenance
  • Amount of bio-load the filter can handle (pounds
    of fish and pounds of feed)

57
Separate Units Strategy
  • Partitions water treatment into a series of
    individually steps
  • Optimizes each step to meet the narrow objective
  • Integrates steps to develop a treatment train

58
Consolidation Strategy
  • Utilize multi-functioning components to
  • Minimize the number of components
  • Improve the stability
  • Reduce costs of components and energy
  • Smaller footprint (less space)
  • Disadvantage is that neither process is optimized
  • If you have space and money the separate units
    strategy is better
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