Technical Memorandum. 1 Summary Findings and Conclusions. SMCSD Headworks, Primary and Secondary Treatment Pre-Design

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Technical Memorandum Water andenvironment SMCSD Headworks, Primary and Secondary Treatment Pre-Design Subject: Prepared For: Prepared by: Reviewed by: SMCSD Dennis Gellerman Steve Clary, Mark Takemoto Date: October 12, 2011 Reference: 0055-003 The purpose of this technical memorandum (TM) is to present the evaluation and preliminary design of the screening facilities to be implemented within the new headworks at the Sausalito-Marin City Sanitary District (SMCSD) Wastewater Treatment Plant (WWTP). This TM is intended to be included as an appendix to the Recommended Project Summary, which includes a summary of major recommendations. All drawings referenced in this TM are bound together as a separate attachment. The TM is organized in the following sections: Section Page 1 Summary Findings and Conclusions... 1 2 Design Criteria... 3 3 Screening Equipment Selection... 4 4 Recommendations... 9 1 Summary Findings and Conclusions Headworks screening facilities typically consist of the following basic components: Channel screen to remove screenable material from the raw wastewater flow stream Grinder to reduce the size of objects that can harm/clog downstream equipment Rake/auger/traveling screen to move the material from the channel up to the operating deck Screening washer/compactor that washes screenings, removes excess water and reduces the amount of organic material collected with the screenings There are a number of headworks screening equipment selection and arrangement options available. Based on the specific requirements of the SMCSD facility and RMC s experience with similar facilities, RMC has developed and evaluated of a range of options. The basic criteria that are used to determine the screening system that provides the best combination of reliability and cost effectiveness are: Flow capacity and redundancy criteria: RMC recommends two separate and automated screening channel systems, each with a capacity of 3 to 4 MGD, and one passive manual coarse bypass screen with a capacity of 10 MGD. This approach would allow one screen unit to handle peak dry weather flows, with one redundant screen. A manual bypass screen with 10 MGD October 2011 1

capacity would also allow instantaneous peak wet weather flows of up to 14 MGD to be screened with one screen out of service. Screen opening: It is recommended that the screen opening width be ¼ inch, and maximum vertical height be 1 inch (or ¼ inch perforated plate design). Openings much larger than these can allow significant material through the screen that would eventually accumulate in the digester. A ¼ inch opening screen will collect more organic material with the screenings, therefore screening washing is recommended to minimize odor generation. The following alternative screening systems were evaluated: Grinder/Sieve Auger Screen Climber Screen Aquaguard Sieve/Auger Screen A summary of the comparison of the screen systems is presented in Table 1. Table 1: Screen Comparison Screen Type Advantages Disadvantages Channel Grinder/Sieve/Screen/A uger Combined grinding, screening, conveying, washing, dewatering and compaction Good organic separation Good screening material removal Grinder maintenance Limited washing of screenings Climber Screen Robust equipment Above-water operation Easy maintenance (unless influent contains significant amount of grease) Coarse-vertical slot Headroom (height) Separate screenings washing/compaction required Plastic teeth break Aquaguard High capture rates Below water bearings Separate screenings washing/compaction required Sieve/Auger Screen Combines screening, conveying, washing, dewatering, and compaction Good screening material removal Limited washing of screenings No grinder upstream to aid with organic separation Recommendation The sieve auger screen is recommended due to better removal of screenings and better washing of screenings. It is recommended that the sieve auger screens have ¼ inch openings and will be designed to handle a minimum combined flow of 6 MGD (3 MGD each). The manual bar rack and bypass channel will be used during flows above 6 MGD, or if a filter screen is out of service during peak wet weather flow. Manual bar screening for flows above 6 MGD should be adequate as most of the debris in the collection system would have flushed into the treatment facility before flow levels rise above 6 MGD. October 2011 2

Without an inflow grinder, a separate washer/compacter/grinder unit will be provided to after the screens. Cleaned and washed screenings from the washer/compacter will be discharged directly to the grit bin. 2 Design Criteria The design criteria for the screenings process is presented in the following sections. 2.1 Flow Capacity A summary of the key design flows for the screening process at current influent flows are presented in Table 1. Table 1: Design Flow Criteria Flow Parameter Average Dry Weather Flow (ADWF) Minimum Diurnal Flow Peak Day Dry Weather Flow (PDWF) 10-Year Event Instantaneous Peak Wet Weather Flow (PWWF) Flow 1.5 MGD 0.25 MGD 3.2 MGD 13 MGD A detailed discussion of the design flows for the new headworks/primary treatment facility and summary of the overall flow schematic can be found in TM 1: Design Criteria. The new headworks will need to accommodate peak flows without equalization because on-site equalization would be located downstream of the headworks processes. In designing the screening system a balance needs to be struck between the channel velocity and screen headloss. Screens are more effective with relatively low velocity through the opening, meaning the wetted area of the screen needs to be relatively large. The consequence of the larger wetted screen area is a relatively large channel area with relatively slow channel velocity, and potential deposition of solids. Channel aeration/agitation could be provided to periodically move the material downstream to the grit chamber. 2.2 Screen Opening Size The screen opening size is an important design factor which determines the amount of materials removed from the raw sewage flow. The smaller openings remove more of the inert materials that are not broken down in the treatment system and which end up in the digester and biosolids. However, the smaller openings also remove biodegradable materials that are putrescible and potentially odorous. In addition, the smaller the screen opening, the larger the screen area needs to be to minimize headloss through the screen. The shape of the opening is also important factor. Several screen types have vertical bars separated by ½ to ¾ inch, but can have over 6 inches between horizontal bars, resulting in a number of common objectionable materials passing through the screen. Perforated holes can remove nearly all of the materials, but can also remove more biodegradable materials. It is recommended that the screens have a width of ¼ inch, and length of 1 inch, or ¼ inch diameter round holes. 2.3 Redundancy The following redundancy criteria are recommended for the screening facilities: October 2011 3

For normal flow conditions including modest wet weather events, provide a completely redundant screen channel system (isolation gate, screen, screening conveyance). For extreme wet weather events no standby automated screen, but have a passive manual bypass screening channel system. Two separate automated screening channel systems each with a capacity of 3 to 4 MGD, and one passive manual coarse bypass screen with a capacity of 10 MGD. This arrangement would provide a peak hydraulic capacity of 14 MGD even if one automated screen is inoperable. 3 Screening Equipment Selection Headworks screening facilities typically consist of the following basic components: Channel screen to remove the material from the raw wastewater flow stream Grinder to reduce the size of objects that can harm/clog downstream equipment Rake/auger/traveling screen to move the material from the channel up to the operating deck Screening washer/compactor that removes excess water and reduces the amount of organics collected with the screened material 3.1 Basic Types of Equipment The types of screens that were evaluated include: Channel Grinder/Sieve Screen /Auger Climber Screen Aquaguard Sieve/Auger Screen These types of screens differ in the type of screen provided, the manner in which they wash and compact the screenings, and the inclusion or exclusion of an integral grinder. The different types of screens are discussed in detail in the following sections. 3.2 Channel Grinder/Sieve Screen/Auger The channel grinder/sieve screen/auger, as produced by JWC and Franklin Miller, combines a channel grinder and a sieve screen auger. An example of this type of screen is shown in Figure 1. These types of screens are able to provide two functions: grind large objects that might clog pumps, and minimize the amount of putrescible material removed by downstream screens. In the case of the new SMCSD headworks, where all the influent flow is pumped to the headworks thereby preventing large objects from reaching the plant, the principal advantage of this type screen is the minimization of putrescible material removed by the downstream screens. October 2011 4

Figure 1: JWC Screen and Grinder Unit The channel grinder/sieve screen/ auger has an integrated screenings washer compactor that delivers compacted screenings up to the operating deck. Depending on the final manufacturer/unit chosen, the grinder unit design may include an adjacent rotating drum screen that rotates to move materials caught on the screen into the grinder. Both the channel grinder screen (if included) and the sieve screen have relatively small openings (approx ¼ inch diameter or larger) that remove nearly all of the objectionable materials from the raw wastewater. Locations where a grinder/sieve/auger unit is in operation in a similar application are Ripon WWTP, San Quentin Prison, Pelican Bay State Prison, and Yolo County Jail. 3.2.1 Rock/Grit Impacts to Grinder Based on discussion with SMCSD staff, the plant occasionally experiences significant grit and rock loads with larger influent flows. There is concern regarding the impact grit/rocks would have on a grinder located in a raw wastewater flow stream. This issue is addressed further in the Screening Equipment Selection section below. The grinder is subjected to all the materials pumped from the Main Street Pump Station and the Fort Baker Pump Station. During extreme flow periods there is potential for heavy grit/rocks to impact the grinder. JWC and Franklin Miller, two grinder manufacturers, were contacted to address the concern regarding the grit/rock load. JWC has stated that occasional rocks and grit will not be a problem other than a little increased wear on the unit. They noted that the grinder is typically offset a few inches from the channel floor, so very heavy rocks could potentially settle out in front of the grinder. In addition, an upstream rock trap could be installed to capture rocks. JWC also offers a service agreement that includes all wear items. The agreement typically is for an initial term length of 5 years (with optional extension) and includes provisions for a temporary replacement unit while the original unit is removed from the channel shipped for maintenance at JWC s southern California facility. October 2011 5

The Central Contra Costa Sanitary District (CCCSD) has several JWC Muffin Monster grinders in their sewage pump stations, including locations that experience high grit loads. Their operations staff indicated that they entered into a service agreement with JWC and that they are happy with the performance of the grinders and the service provided by JWC. At CCCSD s pump station with the highest grit load, they have a several units installed and they rotate between units on a weekly basis to reduce wear on any single unit. An upstream rock trap would help in preventing rocks and heavy grit from entering the grinder and causing wear. Provisions would need to be provided for removing and disposing of the contents of the rock trap, which could be accomplished with a vactor truck. 3.3 Climber Screen Climber Screens are a commonly used type of screen that was developed to provide a low maintenance screening solution without submerged rotating parts such as sprockets and bearings. The Climber Screen is robust and can remove large objects without an upstream grinder. The Climber Screen does not have an integral screenings washing and compaction unit. Therefore, a separate piece of equipment would be required to follow this type of screen. A disadvantage of this screen is the long vertical slot of the bar screen that allows considerable volumes of objectionable materials to pass through the screen and clog downstream processes. There are multiple manufacturers of a climber screen including IDI, FMC, and Vulcan. A typical climber screen can be seen in Figure 2. Locations where climber screens are in operation for similar applications include East Bay Municipal Utilities District (EBMUD), Vallejo Sanitation and Flood Control District (VSFCD), and CCCSD. Figure 2: Climber Screen 3.4 Aquaguard The Aquaguard screen is a self-cleaning, in-channel screening device that utilizes a filter-element system designed to automatically remove a wide range of floating and suspended solids from wastewater. The filter elements are mounted on a series of parallel shafts to form an endless moving belt that collects, conveys and discharges solids greater than the element spacing. Spacings from 1/8 inch to ¾ inch are October 2011 6

available. There are various manufacturers of Aquaguard type screens, including Parkson and Westech. A typical Aquaguard screen can be seen in Figure 3. Figure 3: Aquaguard Screen Movement of the screen can be continuous or intermittent. However, intermittent operations are recommended, which allows a mat of solids to build on the filter-rake elements which increases the solids capture rate. An Aquaguard screen does not have an integral screenings washing and compaction unit. Therefore, a separate piece of equipment would be required to follow this type of screen as discussed below. Aquaguard screens are a widely used type of screen. Some local installations with an Aquaguard include Novato Sanitary District (NSD), Delta Diablo Sanitation District (DDSD), and Central Marin Sanitation Agency (CMSA). 3.5 Separate Screening Washer Compactor For both the Climber Screen and Aquaguard screen, a separate washer compactor would be required. There are various manufacturers of screenings washers and compactors, including JWC, Parkson, and Huber. A typical screenings washer and compactor unit can be seen in Figure 4. October 2011 7

Figure 4: Screenings Washer and Compactor 3.6 Sieve/Auger Screen The Sieve/Auger Screen is a static circular perforated plate screen with a screw auger that performs screening, washing, conveying, compaction and dewatering of screenings in a single unit. It can be installed in a channel or container with an inclination of 35 degrees. Wastewater flows into its open front end and out through the perforation of the screening drum. Floating and suspended materials larger than the perforations are retained. The retained screenings are removed by an auger that conveys the screenings up into a compaction zone to remove free water, and discharge the compacted screenings up to the operating deck. Water sprays are used to provide some separation of organics for the inert screenings. The primary advantages of this equipment are that it is highly efficient (due to the small screen opening) and that it is a relatively simple mechanism. The primary disadvantages of this equipment include the somewhat limited ability to separate organics from inert screenings (since there is no upstream grinder to break up materials), and the inability to handle larger objects. As materials are captured on the screen, the headloss through the screen increases as does the upstream water level. When the upstream water level reaches a certain height, the auger screw begins to rotate. Nylon brushes attached to the auger screw remove material from the screen and move the material up the auger where material is washed and subsequently compacted before being discharged to a dumpster. With the sieve/auger screen as separate washer/compactor would be required. A typical Sieve/Auger screen can be viewed in Figure 5. October 2011 8

Figure 5: Sieve/Auger Screen Some locations where a Sieve/Auger screen is in operation in similar applications are in Eugene, Oregon where it is being used on sluice screenings, and in San Mateo where it is being used on dilute primary sludge (un-screened and un-degritted). 3.7 Screenings Storage and Handling There are several options for the storage, handling, and disposal of the screenings. These options are shown in the Drawing TM 6-1 (attached). One storage option is to have individual bins for screenings from each channel and, when full, the bins would be manually emptied into the grit bin. Another option is to convey the screenings from the screens to a common disposal bin with the grit. This option would likely require at least one, possibly two, screenings conveyor screws. The advantage of combing the screenings and grit is that double handling of the screenings would be eliminated. The disadvantage is that the screenings conveyor screw is another piece of mechanical equipment that requires periodic maintenance. The practicality of this option will be dependent on the siting limitations of the screen and grit facilities. Additional discussion of materials handling and disposal options can be found in the TM 6: Materials Handling, Storage and Disposal and TM 3: Grit. 4 Recommendations The sieve auger screen is recommended due to better removal of screenings and better washing of screenings. It is recommend that the sieve auger screens have ¼ inch openings and be designed to handle a minimum combined flow of 6 MGD (3 MGD each). The manual bar rack and bypass channel will be used during flows above 6 MGD, or if a filter screen is out of service during peak wet weather flow. Manual bar screening for flows above 6 MGD should be adequate as most of the debris in the collection system would have flushed into the treatment facility before flow levels rise above 6 MGD. Without an inflow grinder, a separate washer/compacter/grinder unit will be provided after the screens. Cleaned and washed screenings from the washer/compacter will be discharged directly to the grit bin. Screenings will be transfered to the screenings washer/compactor via a conveyor screw. October 2011 9

4.1 Design Criteria The recommended design criteria for the screening process are presented in Table 2. Table 2: Grit Process Design Criteria Criteria Value Units Screening Process Mechanical Screens Type Sieve auger screen/integral compactor - Number 2 - Openings 1/4 inch Capacity 3 to 4 MGD Manual Screen Type Bar - Number 1 - Screen Opening Width 1 inch Capacity 10 MGD Screenings Washer Compactor Number 1 - Compactor Motor Size 3 HP Grinder Motor Size 10 HP 4.2 Layout and Arrangement Options There are various options for the layout and arrangement of the screening equipment and overall headworks treatment train. Each option is discussed in the TM 2: Siting and TM 6: Materials Handling, Storage and Disposal. Layout and arrangement alternatives are provided as Drawings M-11, M-12 and M-13. 4.3 Screening System Cost The estimated construction cost for the screening facilities is approximately $0.79 million depending on the siting and equipment selections. See the project cost estimate in the Recommended Project Summary TM for more details. 4.4 Operation and Maintenance (O&M) The addition of screening process facilities will require increased operation and maintenance labor as well as power consumption to run the equipment. Operation and maintenance associated with the screening process and equipment is presented in the following sections. 4.4.1 O&M Labor Some annual maintenance will be required for normal servicing and infrequent failures. However, the additional labor is expected to be minor because the systems are automated and rugged. The addition of screens is also expected to reduce labor in other areas of the plant, primarily in the solids system, because there will be less pump clogging and digester cleaning required. Therefore, it is anticipated that the additional process facilities would improve overall plant performance. The estimated impact on SMCSD labor is presented in Table 3. October 2011 10

Table 3: Estimated Required Process Labor Labor Type Process Labor (Hours/week) Process Labor (Hours/Year) Operation 4 208 Maintenance 2 104 Total 6 312 4.4.2 O&M Cost Estimate Adding screening facilities to the SMCSD plant will have a small impact on the O&M costs relating to the following items: Operation and maintenance labor Screenings disposal (covered in TM 6: Materials Handling, Storage and Disposal) Energy Repair parts and service The estimated O&M cost associated with the screening process are presented in Table 4. Table 4: Estimated O&M Costs O&M Items Quantity Units Unit Cost Total Cost Notes Consumables Equipment Consumables $355,000 1.0% $3,600 Mechanical Consumables $30,000 1.0% $300 Subtotal Consumables $3,900 Power Screens 6467 kwh $0.15 $1,000 Aeration Blowers 32335 kwh $0.15 $4,900 Screening Washer 10778 kwh $0.15 $1,600 Subtotal Power $7,500 Labor Operator 4 hr/week $45 $9,400 Maintenance 2 hr/week $45 $4,700 Subtotal Labor $14,000 Chemicals None $- Subtotal Chemicals $- Total Annual O&M Cost $25,500 % of Equipment Purchase Cost % of Mechanical Purchase Cost October 2011 11

Drawings Drawing TM 6-1 Drawing M-11 Drawing M-12 Drawing M-13 October 2011 12