Title: Mechanical Filtration
1Mechanical Filtration
- Hugh S. Hammer, PhD GSCC
- Ron Malone, PhD LSU
- Joe Fox, PhD Texas AM
2Total 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
3Sources 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)
4Problems 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)
5Testing 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)
6Total 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
7Sources 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
8Aquaculture Solids
Solids
FEED
FECES
Uneaten Feed
9Mechanical 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
10Solids 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
11Particle Size Distribution (microns)
Settleable
10-4 10-3 10-2
10-1 1 10
100
Dissolved
Colloidal
Suspended
12SOLIDS REMOVAL PROCESSES AND PARTICLE SIZES
13Impact 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
14Waste 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
15Increased Biochemical Oxygen Demand (BOD)
Oxygen
Oxygen
Oxygen
Heterotrophic Bacteria
Oxygen
Oxygen
Oxygen
16Tilapia
No Fine Solids Capture
17Tiger Barbs
18Settleable 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
19Sedimentation
- Advantages
- Inexpensive
- Works by gravity and doesnt require energy
- Disadvantages
- Only gets largest solids
- Takes a lot of space
- Labor intensive to clean
20SEDIMENTATION
Vh
OUTFLOW
Vs
Settling Zone
INFLOW
Inlet Zone
Outlet Zone
(Vs gt Overflow Rate to settle)
Sludge Zone
21Sedimentation Tanks and Basins
22Sedimentation Tank
23Plate 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
24Centrifuges 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
25Under-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)
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28Airlifts Perform Several Functions
- Circulation
- Aeration
- C02 stripping
- Foam control
29Circulation Options
Circulation
Pump
30Screens
- 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
31Screens
- 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)
32Micro-screen Filters
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34Over-Drain Flow
35Captured Solids
36Microscreen Cleaning Jets
37Granular 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
38Slow 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
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40Rapid 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
41Granular Filters
42Important 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)
43BEAD FILTERS
(a) Propeller-washed
(b) Bubble-washed
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46Propeller-washed Floating Bead Filters
47Broodstock
Return
Anti-siphon valve
Bypass
Sludge View Port
Pressure Gauge
Sludge
Intake
48ADM System Prop-Washed Bead Filters
Motor and Backwash Propeller
Pump
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50Filter Mode
Drop Filters Low Water Loss Floating Bead
Bioclarifiers
Air Bleed Builds Charge
Settled Backwash Waters returned to system
51Backwash mode
Drop Filters Low Water Loss Floating Bead
Bioclarifiers
Released Air Washes Beads
Internal Sludge Capture
52Circulation Aeration Degassing
Solids Capture Biofiltration
Inlet
Airlift
53Cartridge 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
54Sock and Canister Filters
55Diatomaceous 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
56Factors 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)
57Separate 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
58Consolidation 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