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| 30.01 | General Overview |
| 30.02 | Design Criteria |
| 30.03 | Computer Assisted Control Strategies |
| 30.04 | Operating Strategies |
| 30.05 | Troubleshooting |
| 30.06 | Safety |
| 30.07 | Records/Sampling |
The activated sludge process oxidizes and removes soluble and finely divided suspended material that is not removed at the headworks and primary treatment. This is accomplished in the aeration tanks by aerobic organisms during the time the primary treated sewage is detained in the aeration tank. Soluble or finely divided suspended matter is stabilized in the aeration tanks by bacterial oxidation to carbon dioxide, water, and new cellular material. This increased volume of cellular material is removed as a portion of the return activated sludge settled in the secondary clarifiers.
The aeration basins will be constructed in three phases. A group of three basins will be constructed under each phase. Each basin is 160 feet long, 29 feet wide, and 17.7 feet deep. The basins are capable of operating under four different modes: plug-flow, plug-flow anoxic, step-feed and contact stabilization. The preferred mode of operation will be plug-flow anoxic.
All modes introduce return activated sludge (RAS) at the head of the aeration basins; mixed liquor will exit at the opposite end of the aeration basin over the effluent weirs in all modes.
In the plug-flow and plug-flow anoxic process modes, primary effluent will enter over the influent weir gates and exit over the effluent weirs into an effluent channel. In the step-feed and contact stabilization mode, primary effluent will enter through a sluice gate to a 24-inch pipe with adjustable discharge ports to the aeration basin. Air is supplied to all aeration zones within each basin.
Each basin is divided into five aeration zones. The first zone has a baffle wall and mixer for plug-flow anoxic operation. The other four aeration zones contain fine bubble membrane diffusers. The aeration basins are provided with process air by the process blowers. The rate of air supply will be based on dissolved oxygen (DO) in the basin.
The secondary sedimentation process settles the biological floc from the activated sludge mixed liquor allowing the clarified secondary effluent to be withdrawn from the overflow weir. Two clarifiers are provided for the first phase of construction. Four additional clarifiers will be provided for the ultimate buildout plan. A sodium hypochlorite feed point is provided at the weir ring in each clarifier. The purpose of this disinfection point is to allow a periodic shock application to eliminate any biological growth on the weirs.
Each secondary clarifier mechanism has a "ducking arm" type scum skimmer. This type of scum removal system has a full radius withdrawal to a rotating trough which collects scum. The ducking arm directs the scum to the rotating trough and then pivots under the trough to again sweep the circumference of the clarifier. The scum collected in the trough is directed to a secondary scum box.
The design criteria for low pressure Channel Aeration and the Activated Sludge System are presented below.30.02 Design Criteria
CHANNEL AERATION BLOWERS
|
| Number of Units | 3
| Phase 2 | 4 (3 existing, 1 new)
| Capacity | 660 SCFM
| Type | Positive Displacement
|
| AERATION BASINS
|
| Number of Units
| Initial | 3
| Phase 2 | 6 (3 existing, 3 new)
| Ultimate | 9
| Length x Width, Each | 160' x 29'
| Sidewater Depth | 17.7 FT.
| Hydraulic Detention Time (Initial,with 3 units)*
| Maximum Month Flow | 5.5 Hours
| Average Dry Weather Flow | 6.4 Hours
| Peak Hour | 2.1 Hours
| Mixed Liquor Concentration
| Maximum Month Flow | 2,900 mg/l
| Average Dry Weather Flow | 1,800 mg/l
| Solids Retention Time
| Maximum Month Flow | 6 days
| Average Dry Weather Flow | 6 days
| *Ultimate conditions with 9 aeration basins similar
|
| PROCESS BLOWERS
|
| Number of Units | 4 (existing)
| Type | Multi-Stage Centrifugal
| Minimum Capacity, each | 2,000 scfm
| Maximum Capacity, each | 3,900 scfm
| Discharge Pressure | 9.1 psig
| Horsepower, each | 250 hp
| Speed | 3,600 rpm
| Control | Intake throttling
|
| MIXERS
|
| Number of Units | 3
| Phase 2 | 6 (3 existing, 3 new)
| Type | Horizontal, Submersible
| Horsepower, each | 15
|
| AERATION DIFFUSERS
|
| Number of Units (Influent Channel) | 120 (60 existing, 60 new)
| Type | Coarse Bubble
| Number of Units (Zone 1), Phase 1 | 120
| Type | Coarse Bubble
| Number of Units (Zone 1), Phase 2 | 192
| Type | Fine Bubble Membrane
| Number of Units (Zone 2 to 5) | 10836 (7,200 existing, ,636 new)
| Type | Fine Bubble Membrane
| Number of Units (Effluent Channel) | 180 (90 existing, 90 new)
| Type | Coarse Bubble
|
| MIXED LIQUOR RECYCLE PUMPS
|
| Number of Units | 3
| Phase 2 | 6 (3 existing, 3 new)
| Type | Vertical Axial Flow
| Capacity, each | 1,600 gpm
| Horsepower, each | 10
| Speed | 1,800 rpm
|
| NUMBER OF SECONDARY CLARIFIER UNITS
|
| Initial | 2
| Phase 2 | 4 (2 existing, 2 new)
| Ultimate | 6
| Diameter | 95'-0" FT.
| Sidewater Depth | 15 FT.
| Type | Rapid sludge draw-off w/ flocculating well
|
| SURFACE OVERFLOW RATES, INITIAL
|
| Annual Average Flow | (all units in service) 500 gal/sf/day
| Annual Average Flow | (one unit out of service) 670 gal/sf/day
| Maximum Day Flow | (all units in service) 765 gal/sf/day
| Peak Hour Flow | (all units in service) 1,470 gal/sf/day
|
| SOLIDS LOADING RATES
|
| Maximum Month Flow with Maximum RAS | 32 lb/sf/day
| Maximum Day Flow with Maximum RAS | 37 lb/sf/day
| Peak Hour Flow with Maximum RAS | 54 lb/sf/day
|
| CLARIFIER DRIVES
|
| Horsepower, each | 1.0
| | ||||||||||
At the MPWRF, the process blowers supplying air for the activated sludge are controlled through the PLC. The operator selects which control mode the PLC uses to run the blowers using the SCS located in the Marine Park Administration Building. The operator also uses the SCS to monitor alarms and equipment status.
This section tells the operator how to interact with the PLC and the SCS, describes each control loop and describes how and where alarm and equipment status is transmitted.
30.03.b.1. Process Blowers
| Loop Function: | Controls and monitors process blower output by modulating the inlet valve for each blowers. The valve is modulated by a PID flow controller to maintain the air flow setpoint. Monitors blower status and provides a blower fail alarm. |
| Instrumentation: | TSH-11021, TSH-11022, TSH-11023, TSH-11024 (Temperature switch)
(Located at each blower discharge and intake bearing) YSH-11021, YSH-11022, YSH-11023, YSH-11024 (Vibration switch) (Located at each blower discharge and intake bearing) PI-11011, PI-11012, PI-11013, PI-11014, PI-11021, PI-11022,PI-11023, PI-11024 (Pressure indicator) (Located at each blower suction and discharge) IT-11021, IT-11022, IT-11023, IT-11024 (Current transmitter) (Located in each blower local panel) JT-11021, JT-11022, JT-11023, JT-11024 (Power transmitter) (Located at each blower) PDI-11040 (Differential pressure indicator) (Located at the blower inlet filter) FIT-09051, FIT-09052, FIT-09053, FIT-09254, FIT-09255, FIT-09256 (Thermal flow transmitter) (Located in the air header to each basin) PT-11030 (Pressure transmitter) (Located at the blower discharge air header) ICV-11011, ICV-11012, ICV-11013, ICV-11014 (Motor operated flow control valve) (Located on the inlet of each blower) FCV-09050 (Motor operated flow control valve) (Located on the aeration basin air header) |
| Control Devices: | HS-11021, HS-11022, HS-11023, HS-11024 (HOR Handswitch)
(Located on each Local Panel) HS-11021, HS-11022, HS-11023, HS-11024 (SS Push-buttons) (Located on each Local Panel) QL-11021, QL-11022, QL-11023, QL-11024 (Blower ON light) (Located on each Local Panel) QL-11021, QL-11022, QL-11023, QL-11024 (Blower SURGE indication light) (Located on each Local Panel) QL-11021, QL-11022, QL-11023, QL-11024 (High bearing temperature [TEMP] indication light) (Located on each Local Panel) QL-11021, QL-11022, QL-11023, QL-11024 (High vibration [VIB] indication light) (Located on each Local Panel) QL-11021, QL-11022, QL-11023, QL-11024 (Low oil [OIL] indication light) (Located on each Local Panel) IHK-11021, IHK-11022, IHK-11023, IHK-11024 (Inlet throttling valve manual loading station [0 to 100 percent control output] with AUTO/MANUAL selector) (Located on each Local Panel) II-11021, II-11022, II-11023, II-11024 (Blower motor current indicator) (Located on each Local Panel) |
| Alarms: | QA-11020 (All blowers off)
QA-11021 (Blower B-11021 RUN failure) QA-11022 (Blower B-11022 RUN failure) QA-11023 (Blower B-11023 RUN failure) QA-11024 (Blower B-11024 RUN failure) QA-11021 (Blower B-11021 LOCAL failure; high bearing TEMP; excessive VIB; low OIL level; SURGE) QA-11022 (Blower B-11022 LOCAL failure; high bearing TEMP; excessive VIB; low OIL level; SURGE) QA-11023 (Blower B-11023 LOCAL failure; high bearing TEMP; excessive VIB; low OIL level; SURGE) QA-11024 (Blower B-11024 LOCAL failure; high bearing TEMP; excessive VIB; low OIL level; SURGE) PAL-11030 (Aeration basin air header low pressure) PAH-11030 (Aeration basin air header high pressure) |
| PLC/SCS Function: | Monitor blower on status (OOR), QL-11021, QL-11022, QL-11023, QL-11024
Monitor HOR handswitch REMOTE position (OOR), QL-11021, QL-11022, QL-11023, QL-11024 Monitor manual loading station AUTO position, IHK-11011, IHK-11012, IHK-11013, IHK-11014, FHK-09050, FHK-09400 Monitor local blower fail from local panel and provide alarm (LOCAL FAIL), QA-11021, QA-11022, QA-11023, QA-11024 Indicate blower current, IT-11021, IT-11022, IT-11023, IT-11024 Determine blower run failure in REMOTE mode and provide alarm (RUN FAIL), QA-11021, QA-11022, QA-11023, QA-11024 Provide blower LEAD select handswitch (LEAD 1-2-3-4), HS-11020 Provide blower sequencing Modulate blower inlet valve(s), ICV-11011, ICV-11012, ICV-11013, ICV-11014, to control air flow to the aeration basins Provide D.O. process variable select handswitch (1-2-3-A), HS-09040 Modulate the aeration basin air flow bypass control valve, FCV-09400, for split range control Indicate air flow to each cell of aeration basin, FI-09051, FI-09052, FI-09053, FI-09254, FI-09255, FI-09256 Sum air flow to each cell to get total air flow to basins, FI-09050 Indicate air header pressure PI-11030 |
Operation:
| Loop Function: | Monitors aeration basin D.O. and provides an alarm in case of a high or low D.O. condition. |
| Instrumentation: | AIT-09041, AIT-09042, AIT-09043, AIT-09254, AIT-09255, AIT-09256 (Dissolved oxygen probes)
(Located in each of the three aeration basins, movable to zones 2, 3, 4, or 5) AIT-09070, AIT-09270 (Dissolved oxygen probe) (Movable to zone 1 of each aeration basin) |
| Alarms: | QA-09041 (D.O. value AI-09041 is bad)
QA-09042 (D.O. value AI-09042 is bad) QA-09043 (D.O. value AI-09043 is bad) QA-09244 (D.O. value AI-09244 is bad) QA-09245 (D.O. value AI-09245 is bad) QA-09246 (D.O. value AI-09246 is bad) AAL-09041 (Aeration basin low D.O.) AAL-09042 (Aeration basin low D.O.) AAL-09043 (Aeration basin low D.O.) AAL-09244 (Aeration basin low D.O.) AAL-09245 (Aeration basin low D.O.) AAL-09246 (Aeration basin low D.O.) AAH-09041 (Aeration basin high D.O.) AAH-09042 (Aeration basin high D.O.) AAH-09043 (Aeration basin high D.O.) AAH-09244 (Aeration basin high D.O.) AAH-09245 (Aeration basin high D.O.) AAH-09246 (Aeration basin high D.O.) |
| PLC/SCS Function: | Indicate the dissolved oxygen (D.O.) level in each cell of the aeration basin (DO), AI-09041, AI-09042, AI-09043, AI-09244, AI-09245, AI-09246
Average the dissolved oxygen (D.O) level of the three cells (DO AVE), AI-09040 Control aeration basin D.O. level, AIK-09040 Indicate the D.O. level in zone one of an aeration basin (DO), AI-09070, AI-09270 |
Operation:
| Loop Function: | Monitors the secondary clarifier drive unit for high torque and provides an alarm if high torque occurs. |
| Instrumentation: | NSH-14041, NSH-14042, NSH-14243, NSH-04244 (High torque warning switches)
(Located at each secondary clarifier drive mechanism) NSHH-14041, NSHH-14042, NSHH-14243, NSHH-14244 (High torque alarm switches) (Located at each secondary clarifier drive mechanism) |
| Control Devices: | HS-14041, HS-14042, HS-14243, HS-14244 (ON/OFF handswitch)
(Located on MCC-09 and MCC-12) QL-14041, QL-14042, QL-14243, QL-14244 (Clarifier ON light) (Located on MCC-09 and MCC-12) HS-14041, HS-14042, HS-14243, HS-14244 (High torque RESET button) (Located on MCC-09 and MCC-12) QL-14041, QL-14042, QL-14243, QL-14244 (High TORQUE light) (Located on MCC-09 and MCC-12) HS-14041, HS-14042, HS-14243, HS-14244 (Momentary STOP push-button) (Located at the secondary clarifier) |
| Alarms: | NAH-14041 (High torque warning alarm [40% of the ultimate torque] secondary clarifier number 1)
NAH-14042 (High torque warning alarm [40% of the ultimate torque] secondary clarifier number 2) NAH-14243 (High torque warning alarm [40% of the ultimate torque] secondary clarifier number 3) NAH-14244 (High torque warning alarm [40% of the ultimate torque] secondary clarifier number 4) NAHH-14041 (Very high torque alarm [85% of the ultimate torque] secondary clarifier number 1) NAHH-14042 (Very high torque alarm [85% of the ultimate torque] secondary clarifier number 2) NAHH-14243 (Very high torque alarm [85% of the ultimate torque] secondary clarifier number 3) NAHH-14244 (Very high torque alarm [85% of the ultimate torque] secondary clarifier number 4) |
| PLC/SCS Function: | Monitor clarifier on status (ON), QL-14041, QL-14042, QL-14243, QL-14244
Monitor clarifier high torque warning switch and provide alarm, NAH-14041, NAH-14042, NAH-14243, NAH-14244 Monitor clarifier high-high torque switch and provide alarm, NAHH-14041, NAHH-14042, NAHH-14243, NAHH-14244 |
Operation:
The output of the blowers is controlled manually by placing the manual loading station into MANUAL mode and adjusting the position of the inlet throttling valve.
Both the aeration basin air flow and bypass valve are controlled locally by placing the manual loading station into MANUAL mode and adjusting the position of the valve. Under current design conditions, the air flow valve is normally selected to local MANUAL mode and opened 100 percent. The bypass valve is normally placed in local AUTO mode for remote control through the PLC/SCS.
The aeration basin air flow valve is provided for future control of air flow to the three basins currently installed. When aeration basins are added in the future, the control scheme will be modified so that a constant air header pressure is maintained and flow to each set of basins is controlled by the air flow control valves.
The first blower placed into REMOTE mode will function as the LEAD and start immediately. The second and third blower placed in REMOTE mode, can be started through the SCS CRT by the operator. All the blowers placed in REMOTE can also be stopped throught the SCS CRT. The LEAD blower may be changed by operations through the SCS CRT. If a blower is not started by the operator and it is in REMOTE, it functions as a standby and will come on should another blower fail. Upon power failure, only the channel blower that is designated as the LEAD will re-start.
In the REMOTE mode, the blowers function in a LEAD, 1st LAG, 2nd LAG, and STANDBY sequence as defined below. The output of the blowers is controlled, automatically by placing the inlet valve manual loading station into AUTO mode. The air flow split between the basins is controlled by manual valves on the individual basin air headers.
When the blowers are in REMOTE mode and the inlet valve manual loading stations are in AUTO mode, there are three modes of control available through the PLC/SCS, MANUAL, AUTO, and CASCADE. The mode selected is used to control all four blowers. There is a PID loop faceplate for each blower at the SCS CRT allowing operating personal to monitor air flow and blower performance and to make control changes as defined below. The PLC/SCS is programmed for bumpless transfer between modes. This means that the air flow to the basins will not make an instantaneous change when the mode of the controllers in change between MANUAL, AUTO and CASCADE.
When in MANUAL mode, each blower can be individually started and stopped and have its inlet valve position adjusted through the SCS CRT.
When in AUTO mode, the inlet valve for each blower is modulated by a PID flow controller to maintain an air flow setpoint to the three basins. The sum of the air flows to each basin is used as the process variable for the PID controller.
When in CASCADE mode, the air flow PID controller setpoint is "cascaded" from or set by the output of a D.O. PID controller. The D.O. PID controller adjusts the air flow setpoint to maintain a D.O. setpoint. The process variable for this loop is selected through the SCS CRT. Options include, basin 1, basin 2, basin 3, or average basin D.O. If average D.O. is selected, an alarm is generated if one of the probe readings is significantly different from the other two. That probe reading is removed from the average calculations until the alarm is reset at the SCS CRT.
The blowers are sequenced automatically when AUTO or CASCADE mode is selected. Any time a blower is started automatically, its inlet valve is initially at its minimum open position. The blower selected as LEAD operates continuously. The 1st LAG blower is started when the LEAD blower reaches its maximum capacity and the system demand continues to increase. This is determined when the output of flow controller is greater than 99 percent and the flow controller setpoint is greater than the capacity of one blower for a preset time. The output of the flow controller is then initialized to a value where two blowers deliver the same capacity as a single blower. The LEAD blower and 1st LAG blower then operate in parallel. The 2nd LAG blower is started when both LEAD and 1st LAG blowers reach their maximum output and the system demand continues to increase. This is determined when the output of flow controller is greater than 99 percent and the flow controller setpoint is greater than the capacity of two blowers for a preset time. The output of the flow controller is then initialized to a value where three blowers deliver the same capacity as two blowers. All three blowers will then operate in parallel.
The blowers are sequenced off in reverse order as the system demand decreases. The 2nd LAG blower is stopped when the flow controller setpoint falls within the maximum capacity of two blowers. The value of the flow controller setpoint at which this happens is lower than the value of the 2nd LAG blower start setpoint to prevent cycling. As the system demand continues to decrease the 1st LAG blower is stopped when the flow controller setpoint falls within the maximum capacity of a single blower. No initialization of the flow controller output occurs when stopping blowers. The inlet valves of the blowers are set to their initial minimum open position when the blowers are stopped.
The LEAD blower is selected by a handswitch on the SCS CRT. The following are the blower sequences based on which blower is operating as LEAD:
In order to be included in the automatic sequence, a blower must be selected to REMOTE and the local panel manual loading station for the inlet valve must be selected to AUTO. If a blower is called to run and the switches are not in these positions, the next blower in the LEAD/LAG sequence will be started if it is selected to REMOTE and its inlet valve control manual loading station is in AUTO. In REMOTE mode, upon failure of the LEAD or a LAG blower, the STANDBY blower is started.
Split range control is programmed to prevent blower surge when air flow demands are between the range of one and two, or two and three blowers. When operating in AUTO or CASCADE mode, the air flow controller adjusts the blower inlet valve(s) in an attempt to maintain the air flow controller setpoint. If the controller closes the inlet valves to their minimum open position, the PLC/SCS will switch to split range control. In split range control, the bypass valve is modulated to increase air flow demand so that the blower(s) move away from surge conditions. The output from the air flow controller is reversed and is used to modulate the bypass valve from its minimum open position to its full open position. Split range control is stopped if the air flow controller setpoint decreases so that a blower can be stopped or if the setpoint increases so that the controller output increases above the minimum open position of the inlet valves.
Surge conditions are identified by the blower current reading(s) approaching the current value at which the blowers experience surge. The blower surge current values will be correlated with blower inlet valve position. For example, an inlet valve position of 15 percent may move the blower(s) and blower current into surge conditions. This then would be the inlet valve minimum open position.
The bypass valve is also used to control the air flow to the aeration basin effluent channel. A minimum air flow to this channel is required to prevent settling of solids and to prevent plugging of the diffusers. The minimum open valve position for the bypass valve is determined when a single blower is delivering its minimum air flow rate and the air requirements of the effluent channel are still being met.
A clarifier is shutdown if the drive mechanism over torques as sensed by the high-high torque switch. This interlock is reset by pressing the high torque reset button. The clarifier manufacturer will provide control panel for the scum withdrawal system. This will allow the operators to adjust the amount of secondary scum generated by selecting the degree to which the scum trough is rotated into the water surface to collect scum.
Equipment protection interlocks -- alarms will be activated when the torque load reaches 40 percent of the ultimate torque. If the torque continues to increase, up to 85 percent of the ultimate torque, the clarifier drive motor will be de-energized.
Note: Normal plant operation will use the PLC and the SCS CRT to enter setpoints, select equipment operating modes and monitor equipment status. If a process can be controlled manually through the SCS CRT then this will also be included in this section. Local control of equipment will be covered under Section 30.04.c., Alternate Operating Conditions.
The Process Blowers can be run either in AUTO or MANUAL through the SCS/PLC system. These SCS CRT controls are located on the Process Blower Control screen. With the IHK control set to AUTO, the operator can select MANUAL, AUTO (SCFM) or D.O. PID control for blower output, and LEAD blower sequencing. In AUTO and D.O. modes, the PLC controls the position of the blower inlet control valve and the number of blowers on line based on either a SCRM or D.O. setpoint. In MANUAL mode, the Operator sets the position of the inlet control valve and runs the number of blowers needed to meet air demand needs. The operator uses the SCS CRT controls located on the IHK control screen to set the inlet conrol valve position in percent. Start/Stop buttons will appear on the screen for each blower when the MANUAL mode is selected. Equipment Status Table 30.04.b.1. summarizes the proper equipment configuration for normal plant operation.
|
| Equipment Description | Status
| B-11021 (Blower #1) | HOR Handswitch to REMOTE at LP-11021
| B-11022 (Blower #2) | HOR Handswitch to REMOTE at LP-11022
| B-11023 (Blower #3) | HOR Handswitch to REMOTE at LP-11023
| B-11024 (Blower #4) | HOR Handswitch to REMOTE at LP-11024
| Blower Discharge Valves | Open on all blowers
| FCV-09050 (Aeration Basins Flow Control Valve) | REMOTE
| FCV-09400 (Aeration Basin Air Flow Bypass Control Valve) | REMOTE
| | |
| IHK-1102X (Inlet throttling valve manual loading station) | Set to AUTO |
| Blower Mode | Select either AUTO or D.O. modes and enter the desired setpoint Select LEAD blower sequence. |
| IHK-1102X (Inlet throttling valve manual loading station) | Set to AUTO |
| Blower Mode | Set to MANUAL. Operator must select the number of blowers to run and manually adjust the inlet throttling valve to meet the air demand. |
There is no SCS CRT control or monitoring available on the butterfly valves directing air flow to the individual aeration basin air headers or for the butterfly valves used to balance flow to each aeration zone. The operator is responsible for adjusting these valves to equalize air flow split between aeration basins and to taper air flow along the length of each basin. The operator is also responsible for putting the D.O. probes in the proper zone within each aeration basin.
The operator does not have the ability to start or stop a secondary clarifier through the PLC/SCS system. However, the operator can monitor whether a clarifier is on line and if a high torque condition exists. This information can be found on the Secondary Clarifier screen on the SCS. Equipment Status Table 30.04.b.3. summarizes the proper equipment configuration for normal plant operation.
|
| Equipment Description | Status
| M-14041 (Secondary Clarifier #1) | HS-14041 turned ON at MCC-09
| M-14042 (Secondary Clarifier #2) | HS-14042 turned ON at MCC-09
| M-14243 (Secondary Clarifier #3) | HS-14243 turned ON at MCC-12
| M-14244 (Secondary Clarifier #4) | HS-14244 turned ON at MCC-12
| | |
The ducking scum skimmers are neither operated nor monitored through the PLC/SCS system. Rather, the operation is totally controlled through local panels LP-14041 and LP-14042 located on each secondary clarifier. To operate the skimmers the operator must set the scum trough rotation delay timer, the scum trough open time and the scum collection arm pass counter. Once adjusted these setting should not be changed unless there is a change in scum removal efficiency. Equipment Status Table 30.04.b.4. summarizes the proper equipment configuration for normal plant operation.
|
| Equipment Description | Status
| LP-14041 (Scum Skimmer Local Panel) | HS-14041 set to AUTO
| LP-14042 (Scum Skimmer Local Panel) | HS-14042 set to AUTO
| LP-14243 (Scum Skimmer Local Panel) | HS-14243 set to AUTO
| LP-14244 (Scum Skimmer Local Panel) | HS-14244 set to AUTO
| | |
Blank.
A contingency Plan is written to handle an unpredictable occurrence that has a reasonable chance of happening. Most Contingency Plans deal with situations where having a written procedure can help prevent loss of a unit process, handle a process upset or respond to a hazardous situation. The following is a list of Contingency Plans developed for the Activated Sludge process. The plans are kept in the Contingency Plan Notebook located in the Operator Laboratory and the Shift Supervisor Office.
A Standard Operating Procedure (SOP) is written to handle operator activities performed on a regular but not necessarily daily basis. Most SOPs deal with potentially hazardous activities making it important that a written, step-by-step procedure be available. The following is a list of SOPs developed for the Activated Sludge process. The procedures are kept in the SOP Notebook located in the Operator Laboratory and the Shift Supervisor Office.
See Section 75 Maintenance Plan for trouble shooting dealing with the operation of the process blowers, aeration basin mixers, mixed liquor recycle pumps, and secondary clarifier drive mechanism.
Refer to Table 30.05.a.1. for troubleshooting procedures dealing with foaming problems in the aeration basins.
Refer to Table 30.05.a.2. for troubleshooting procedures dealing with sludge bulking problems in the secondary clarifiers.
Refer to Table 30.05.a.3. for troubleshooting procedures dealing with nitrification problems.
|
| Observation | Probable Cause | Solution
| Stiff white billowing or sudsy foam on aeration basin surface. | Young sludge in an overloaded aeration tank (low MLSS). NOTE: This problem usually occurs during process startup and is only temporary. | First calculate F/M. If the F/M is high, reduce or suspend wasting until target F/M is reached.
| Excessive solids carryover from the secondary clarifier. | Check RAS rate to verify that it is adequate to minimize solids carryover.
| High/low D.O.'s in aeration basins. | Try to maintain D.O. levels between 2.0 and 3.0 mg/L. Also verify that adequate mixing is being provided in the aeration basins.
| Toxic upsets (metals, bactericide, high/low pH levels). Will likely cause an extremely low SOUR (less than 5 mg/g-hr). | Waste toxic sludge from the system. Obtain seed sludge from the Westside Plant.
| Shiny, dark brown foam on aeration basin surface. | Aeration basin approaching an underloaded (low F/M) condition due to insufficient wasting. | Increase the wasting rate by no more than 10%/day until a light tan foam is observed on the aeration basin surface.
| Imbalance of return rates to aeration basins. | Equalize return rate to each aeration basin.
| Thick, scummy, dark brown foam on aeration basin surface. | Aeration basin is critically underloaded (F/M too low) due to improper wasting. | Increase the wasting rate by no more than 10%/day until a light tan foam is observed on the aeration basin surface.
| Scum and grease entering the aeration basins. | Check primary scum collection system and confirm proper operation.
| Greasy, dark foam that is strong and carries over into the clarifier. | Filamentous bacteria (Nocardia). | Control influent and recycled greases and oils. Lower MCRT to remove bacteria from system. If possible, physically remove aeration basin foam and clarifier scum.
| Moderate amount of fresh light tan foam. | Not a problem. Usually a sign of a well running process.
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| Observations | Probable Cause | Solution
| Clouds of billowing sludge rising and extending throughout the clarifier. Mixed liquor settles slowly and compacts poorly in settleometer test. Few or no filaments present. | Toxics present causing dispersed growth bulking. High F/M bulking. | Decrease wasting. Decrease return rate. Use polymer to aid settling. NOTE: Cl2 addition is not effective in correcting bulking due to dispersed growth.
| Same as above except that numerous filaments are present. | Low D.O. in aeration basins causing filamentous bulking. | If D.O. is low throughout the aeration basin increase aeration rate. If D.O. is low in some spots but good in others, balance the air distribution within the basin. If this doesn't correct the problem then clean diffusers. | Decrease F/M, if possible. Chlorinate RAS at 1 to 10 lb/day/1000 lb MLSS, starting low and working up. Closely monitor settleability and turbidity. Add polymer to help relieve settling problems. Septic influent with sulfides. | Verify that the channel aeration system is working properly.
| Verify operation of the aerated grit removal system. | |||
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| Observations | Probable Cause | Solution
| Decrease in system pH with loss of nitrification. | Insufficient addition of lime to offset alkalinity destruction during nitrification. | Check alkalinity in the secondary effluent. If less than 20 mg/L, start adding lime to the aeration basin influent.
| Addition of an acidic waste to the sewer system. | Check influent pH and alkalinity. If low, contact Industrial crew to begin tracing source.
| Unable to completely nitrify. Effluent ammonia level exceeds permit levels. | D.O. concentration is limiting nitrification. | D.O. in aeration basins should be no lower then 2 mg/L. If D.O.'s are low, increase aeration or decrease loadings.
| Cold temperatures are limiting nitrification. | Decrease loadings on the system, increase MLVSS in the system by raising MLSS concentration or by putting another aeration basin on line.
| Nitrifier fraction too low in the aeration basins. | Check to see if solids are escaping from the secondary clarifier. Add polymer to enhance settling if necessary.
| Check wasting rate. If possible, decrease wasting until system stabilizes. Low alkalinity. | Check influent alkalinity. If low increase alkalinity.
| If zone 1 of the aeration basins is not being operated as an anoxic zone, begin anoxic zone operation to increase alkalinity. Slow settleability of the mixed liquor. | Toxics present. | Check SOUR and the presence of inactive protozoa with the microscope. If the SOUR is low and inactive protozoa are present, contact the Industrial crew to trace the source.
| Bulking due to filamentous organisms. | Check for the presence of filaments under the microscope. Also check D.O. and pH. See Table 30.05.a.2., second observation.
| Pin floc in the clarifier effluent. | Long MCRT. High nitrifier fraction causing rapid settling. | Decrease MCRT and reduce nitrifier fraction by increasing wasting rate.
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The operator is responsible for reviewing the SOP on Entering the Aeration Basin Influent Channel. A confined space entry form must be filled out and properly signed before entry into the channel.
The operator is responsible for reviewing the SOP on Entering and Cleaning the Aeration Basins. A confined space entry form must be filled out and properly signed before entry into any basin.
The operator is responsible for reviewing the SOP on Entering the Aeration Basins Effluent Channel. A confined space entry form must be filled out and properly signed before entry into any channel.
The operator is responsible for reviewing the SOP on Entering and Cleaning the Secondary Clarifiers. A confined space entry form must be filled out and properly signed before entry into the clarifier.
30.07 Records/Sampling
30.07.a. Sampling Schedule
NAME FREQUENCY TYPE LOCATION |