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Presentation for MWEA Process Committee Seminar November 6, 2013 SCREENING AND CONSEQUENCES Tom Grant, Hubbell Roth and Clark Sandra Diorka, Delhi Charter Township Need for Project Class A Sludge Anaerobic Digestion System Heat Exchangers


  1. Presentation for MWEA Process Committee Seminar November 6, 2013 SCREENING AND CONSEQUENCES Tom Grant, Hubbell Roth and Clark Sandra Diorka, Delhi Charter Township

  2. Need for Project  Class A Sludge Anaerobic Digestion System Heat Exchangers Plugging

  3. Plugging Heat Exchangers  All raw sludge is macerated such that fibers, plastics, etc. are relatively small, about ¼” wide x 3” to 6” long  During sludge recirculation and pumping through 1 1/4” and 3” diameter heat exchanger tubes, small pieces become entwined and form ropes that plug the heat exchangers  Heat exchangers required cleaning every other day

  4. Plugging Heat Exchangers

  5. Existing Not Effective  Existing headworks grinding with capture was not effectively removing screenable materials from wastewater  Requires seasonal cleaning of primary clarifiers and disposal of wet settlings to drying beds  Causing early wear on POTW equipment  Excessive labor spent removing rags from all process equipment  Wasting pumps  Telescopic valves  Decant valves  Digester heat exchangers

  6. Existing Not Effective

  7. Existing Not Effective  Removal of about 40 pounds wet material per day

  8. New Screen Selection: Site Visits, Round 1  Traditional bar screens  Visited Michigan WWTPs to view their headworks screens:  South Lyon, ¼” bar  Grand Rapids, ¼” bar

  9. Bar Screen Observations  During site visits noticed:  Bar screens had excessive pass through  Equipment had grease balls and strings hanging  Resulting screenings were very dirty  Bar screen room and environment was gross  Primaries, aeration tanks, and secondaries had floaters  Conclusion: Bar screens are not so good. What else can we get?

  10. Pilot Testing at POTW  How do we pick between round holes and slots (bar screen)? How big should the holes be?  Devised an in house experiment  Fabricated a slide gate with four different “screens” built in  1/8 inch round hole (perforated plate)  1/4 inch round hole  1/4 inch “bar” hole  Window screen (around 1mm hole size)

  11. Pilot Testing at POTW  Placed each gate in the influent channel for a specified time  Weighed the material collected  Window screen was considered “100%” capture  Roughly 8000 pounds per day  Round holes collected roughly 4 times the amount of material as the bar or slot shaped openings  Conclusion: We want round holes!!

  12. New Screen Selection: Site Visits, Round 2  North Kent, 1 to 3 mm drum screen

  13. New Screen Selection: Site Visits, Round 2  Kalamazoo, 6 mm bandscreen Screen entrance is sealed to channel Flow In Flow Out

  14. Discovered and Purchased U.K. Study  Purchased “National Screen Evaluation Facility, Inlet Screen Comparative Report” performed between 1999 and 2011 by the UK Water Industry Research  Installed and compared the performance of 27 different headworks treatment products  Finescreen  Stepscreen  Combined screen (bar or round with processing)  Bandscreen  Reported % capture of material  Maintenance frequency

  15. Finescreen • Screen rotates around to carry stuff to the top • Can have round or bar openings

  16. Stepscreen • Like a fine screen • Steps move and transport stuff to the top – body of the screen holds still

  17. Discovered and Purchased U.K. Study  Bandscreens showed the best performance  Highest screen capture rate  Lowest risk of “pass through” or “carry over” because of seal between opening and the channel  Study showed two brands had the highest screen capture rate  Screens incorporating slots or bar spacing showed the lowest performance  Conclusion: We want one of the bandscreens with the highest capture rate!

  18. Site Visits Round 3  Made a three day trip to visit four additional screens  Ishpeming, MI – Jones and Atwood band, 6 mm holes  Sheboygan, WI – Brackett Green band, 6 mm holes  Madison, WI – Brackett Green band, 6 mm holes  Fond du Lac, WI – JWC Fine Screen, 3 mm holes

  19. Site Visits  Ishpeming

  20. Site Visits  Sheboygan

  21. The Final Decision  How did we decide?  The cleanest end product  3mm because  Madison had 6mm hole size with the same type of heat exchanger  Heat exchangers still plugged  Fond du Lac had 3mm hole size with the same type of heat exchanger  Heat exchangers did NOT plug!!

  22. What Happened After ?  Heat exchangers no longer routinely cleaned  Primaries have no rags or floating “salad”  Grease hauled less often (contains only grease)  Aeration tanks do not have to be “skimmed”  No more condoms  Wasting pumps no longer need to be routinely cleaned  Sludge storage decant valves have remained clean  Telescopic valves no longer have to be cleaned

  23. Screenings Production 1200 1000 800 600 400 200 0

  24. Raw Sludge % Volatile 88.0 86.0 84.0 82.0 80.0 78.0 76.0 74.0 72.0 After Before 70.0

  25. Grit Production 500 450 400 350 300 250 200 150 100 50 0

  26. Before – NOT Gritty

  27. After – Actually Grit

  28. Engineering and Construction Design Engineering  2 screens, each handle 6 mgd, bypass/overflow manually cleaned channel 5 mgd  Tight site – fit between existing influent screw pumps, grit tank and primary clarifiers  Existing hydraulic grade line is fixed  Poor soils for building & channels foundation

  29. Tight Site

  30. Poor Soils Helical Screw Piles Foundation

  31. Construction  Extended schedule due to piles, originally June 2012 completion, first screen started in October 2012  Alternate bypass

  32. Construction Gravity Bypass

  33. Construction

  34. Construction

  35. Construction

  36. Construction

  37. Results

  38. Results

  39. Questions??

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