Wastewater Engineering 3
Methods of Expressing Pollutant Concentrations
- mg/L (milligrams per liter)
- ppm (parts per million)
- PPD (parts per billion)
- Change of mass over time is a minor factor in reactions.
- Common in wastewater treatment; reactions are non-constant.
Effluent Stream Calculation
- Q{in}C{in} = Q{out}C{out} + KVC
- (10 \frac{m^3}{s})(20) + (15 \frac{m^3}{s})(40) = (15 \frac{m^3}{s})(C)
- C = 26.67
Mass Accumulation Rate
- Q{in}C{in} = Q{out}C{out} + KVC
- (1 \frac{m^3}{s})(5 \frac{mg}{L}) + (0.25 \frac{m^3}{s})(10.01 \frac{mg}{L}) = 0.26 \frac{m^3}{s} (C)
- C = 3.35 \frac{mg}{L}
Chemical Reaction Rate/Half Life
- t_{1/2} = \frac{0.693}{k}
- For t_{1/2} = 3: k = \frac{0.693}{3} = 0.23
- For t_{1/2} = 12: k = \frac{0.693}{12} = 0.058
Plug Flow Reactor (PFR)
- \frac{C}{C_0} = e^{-kt}
Complete Mix Process
- t = \frac{V}{Q}
- \frac{C}{C_0} = \frac{1}{1+kt}
- 0.30 = \frac{C0e^{-kt}}{C0} \implies 0.30 = e^{-kt}
- 0.5 = e^{-\frac{kt}{Q}}
- t_{1/2}= \frac{0.693}{k}
- 0.5 = e^{\frac{-V}{Q}} \implies \frac{V}{Q} = \frac{0.693}{0.5} = 0.30
Wastewater Engineering
- Scum: Consists of grease, oil, plastic, leaves, rags, hair, and other floatable material.
- Raw sludge or primary sludge: The mass of settled solids.
Primary Treatment Removal Efficiency
Parameter | Metcalf & Eddy | Frank Spellman |
---|---|---|
Settleable Solids | 90-95% | 90-95% |
Suspended Solids | 50-65% | 40-60% |
BOD | 20-35% | 25-35% |
Sedimentation
- Oldest and most widely used unit operation in wastewater treatment.
- Process used in both primary and secondary wastewater treatment where gravity pulls particles to the bottom of a tank (settling).
Primary Sedimentation
- Objective: To remove readily available settleable solids and floating materials, reducing the suspended solids content.
- Settling tanks receiving raw wastewater before biological/chemical treatment are called primary tanks or clarifiers.
Short-Circuiting
- Hydraulic condition in a tank where the travel time is less than the flow-through time.
Types of Sedimentation Tanks
- Septic Tanks
- Two-Story (Imhoff) Tanks
- Plain Settling Tanks (Clarifiers)
- All three can be used for primary treatment; plain settling tanks are normally used for secondary or advanced wastewater treatment processes.
Septic Tanks
- Prefabricated tanks that combine settling, skimming, and anaerobic digestion.
- Provide long settling times (6 to 8 hours or more) but do not separate decomposing solids from the wastewater flow.
- Solids are discharged with the flow when the tank becomes full.
- Suitable for small facilities only.
Two-Story (Imhoff) Tank
- Similar to a septic tank in removing settleable solids and anaerobic digestion.
- Consists of a settling compartment, a lower compartment for digestion, and gas vents.
Plain Settling Tanks (Clarifiers)
- Optimizes the settling process.
- Sludge is removed for processing in downstream treatment units.
- Flow enters, slows, and distributes evenly, then leaves over the effluent weir.
- Detention time: 1 to 3 hours, with a 2-hour average (Spellman).
Rectangular Clarifier
- Solids are scraped to one end.
- Favored when space is a constraint; economical piping arrangements.
- Multiple units should be designed for independent operation.
Circular Tanks
- Theoretical flow pattern is radial.
- Wastewater is introduced in the center or around the periphery (center-feed is more common).
- Larger tanks have a central pier that supports equipment.
- Typical center feed tank has a vertical inlet pipe with ports that transmit flow to the feed well (flocculation center well).
- Energy dissipating inlets (EDI) distribute flow within the feedwell and increase flocculation.
- Flow-splitting device is placed between redundant clarifiers.
Accessories and Parts of Circular Clarifier
Part | Purpose |
---|---|
Influent Control Gate | Throttles or stops the flow to the clarifier |
Influent Channel or Pipe | Transports wastewater to the clarifier |
Influent Well | Receives the flow, reduces flow velocities, and distributes flow evenly across the upper portion of the clarifier; small circular compartment in the top center of the clarifier. |
Effluent Weir | Ensures equal flow; designed for small surface elevation adjustments. |
Effluent Trough or Launder | Collects the settled wastewater flowing over the weirs and conveys it from the clarifier. |
Scum Skimmer Arm | Skims or collects floating materials and moves them to the scum trough. |
Scum Trough | Receives the floating material scraped from the surface. |
Scum Pipe | Allows the collected scum to flow to a scum tank or pump. |
Drive Unit | Causes the collector to rotate. |
Vertical Drive Cage | Transmits power from the drive unit to the sludge collector mechanism. |
Sludge Collector Mechanism | Drags settled solids across the clarifier bottom to the sludge collector pit or sump. |
Blades and Scraper Squeegees | Scrape sludge from the bottom of the clarifier to the sump. |
Sump | Collects the sludge before withdrawal. |
Sludge Withdrawal Pipe | Removes the sludge from the clarifier and usually connected to a sludge pump. |
Primary Tank's Detention Time
- 1-2 hours
Factors Affecting Settling
- Time: Must be long enough for particles to settle.
- Long detention times cause:
- Solids to become septic
- Solids to float to the surface
- High SS levels in primary effluent
- Odors in primary effluent
- Long detention times cause:
- Volume: Must not exceed tank capacity.
- Types of solids and characteristics of wastewater.
- Flow rate
- Temperature
Design Criteria of Primary Sedimentation Tanks
Types of Settling Phenomena in Wastewater
- Discrete: Particles settle without interaction, occurring under low solids concentration (e.g., sand removal).
- Flocculant: Particles initially settle independently but flocculate, increasing settling velocity as they aggregate.
General Design Criteria
Parameter | Range | Typical |
---|---|---|
Detention Time, h | 1.5-3 | 2 |
Overflow Rate, m³/m²/day | ||
* Average | 24-32 | |
* Peak Flow | 32-48 | |
Weir Loading, m³/m·day | 80-120 | 100 |
Length to Width Ratio | 4:1 to 10:1 | 4:1 |
Accessories
- Scum Collector
- Sludge Collector
- Primary Sludge Pumps
Additional Design Criteria
Parameter | Value |
---|---|
No. of Tanks | 2 or more |
Type of Tanks | Circular/Rectangular |
Tank Bottom Slope | 60-150 mm/m |
Speed of Sludge Scraper | 0.02-0.05 rpm |
Tank Dimensions
Dimension | Range | Typical |
---|---|---|
Rectangular Length (m) | 15-100 | 30 |
Width (m) | 3-30 | 10 |
Depth (m) | 2.5-5 | 4 |
Circular Tank Diameter (m) | 3-60 | 30 |
Depth (m) | 3-5 | 4 |
Bottom Slope (mm/m) | 0.02-0.05 | 0.03 |
Coagulant(+)
- Used to remove charged particles, enabling them to attract and settle.
Calculations
- Circular Surcharge:
Surcharge = \frac{15,071,000}{3,989} \approx 3,778 - Waste Charge: 5,000 = 15,0719 to
\ - 190 mg/L BOD
- 225 mg/L BOD
- 210 mg/L SS
- 365 mg/L SS
- Average Flow
- Peak Flow
SOR
- SOR = \frac{77.98 m^3/day}{44.56 m^2} = 1.75 \frac{m}{day}
- BOD removal = \frac{2100}{0} = 89.5 \%.
- SS Removal = (X-X)(%) \implies \frac{(365-3d)}{8207.5 kg/day} \implies 8207.5 kg/day \implies 5:1
- A = \frac{E}{V} = 709.83 m^3
Continuous-Flow Stirred Tank Reactor (CFSTR)
- Also known as Completely-Mix Reactor.
- Reactants entering the reactor are dispersed immediately, and products flowing out are continuous.
- C_o
- Q_o
- V
- C_e
Arbitrary Flow Reactor (AFR)
- Any degree of partial mixing between plug-flow and complete-mix.
Packed Bed Reactor (PBR)
- Filled with inert packing media for biomass growth.
- Wastewater flows continuously in and out.
- Used for attached growth treatment systems.
- Influent C(2)
- Effluent.
Fluidized Bed Reactor
- Filled with packing material that expands and gets fluidized when wastewater moves upward.
- FBR or FBBR (Fluidized Bed Biofilm Reactor): Combination of attached growth and suspended growth.
- Biological slime is developed and maintained on a solid support medium.
Types of FBR:
- Captor:
- Biomass is grown inside polyester foam pads; pads can be periodically removed and biomass squeezed.
- Oxygenation is achieved using a simple sparger.
- Developed by Simon Hartley Captor.
- Oxitron:
- Sand particles are used as a support medium; sand is allowed to overflow, cleaned, and recycled.
- Uses high-purity oxygen dissolved into the influent stream.
- Developed by Dorr Oliver.
Modification of Activated Sludge Process (Secondary Treatment)
Process Name | Type of Reactor |
---|---|
High Rate Aeration | Plug Flow |
Contact Stabilization | Plug Flow |
Conventional Plug Flow | Plug Flow |
Step Feed | Plug Flow |
Complete Mix | CFSTR |
Extended Aeration | Plug Flow |
Oxidation Ditch | Plug Flow |
Batch Decant | Batch |