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BIOCHAR PRODUCTION FROM SEWAGE SLUDGE AND MICROALGAE COMBINATION: PROPERTIES, SUSTAINABILITY AND POSSIBLE ROLE IN A CIRCULAR ECONOMY A.G. Capodaglio, G. Bernardi, S. Bolognesi, A. Callegari Department of Civil Engineering & Architecture,


  1. BIOCHAR PRODUCTION FROM SEWAGE SLUDGE AND MICROALGAE COMBINATION: PROPERTIES, SUSTAINABILITY AND POSSIBLE ROLE IN A CIRCULAR ECONOMY A.G. Capodaglio, G. Bernardi, S. Bolognesi, A. Callegari Department of Civil Engineering & Architecture, University of Pavia, Italy

  2. STATEMENT OF PROBLEM -1 Municipal WWTPs excess sludge production expected in 2020 for the entire EU is about 13 Mt. Assuming a dried ≈4x sludge water content of 30%, the total volume of sludge to be disposed yearly would be just short of the volume of FOUR Cheope’s PYRAMIDS!

  3. Main sludge disposal options in EU member states QUESTION: WHAT IS THE MOST SUSTAINABLE OPTION Source: Eurostat, 2016

  4. STATEMENT OF PROBLEM -2 nt technological advances have postulated a paradigmatic change in WW treatm hnologies: example the Almeria (Spain) WWTP where WW is treated by a mixture of eria and microalgae. antages Disadvantages one (or less) O 2 supply Need close to 365 sunny days/year eria remove C “Sludge” is a mix of m-algae and bacteria e remove N, P and supply O 2 Diffjcult to dewater ge/algal mix can be digested or converted to fertilizer May not solve the residuals issue

  5. POSSIBLE SOLUTION EXCESS MUNICIPAL ALGAE WASTEWATER SLUDGE FROM WW TREATMENT PYROLYSI S OTHER EXCESS CROP RESIDUALS We postulate that co-pyrolys of EMWS, microalgae, and (eventually) Other excess crop residues (i.e. wine-making residuals, rice straw, roadside grass clippings, etc) is not only efgective in

  6. PYROLYSIS PRODUCTS BIO-OIL BIOCHAR SYNGAS CO 2 H 2 CO HIGH C LIMITED AMPLE APPLICATON CONTENTS RELEASE OF POSSIBILITIES & LONG- TERM HEAVY METALS STORAGE

  7. EXPERIMENTAL SETUP TYPE ‘D’ TYPE ‘C’ TYPE “A” TYPE “B” SAMPLE SAMPLE SAMPLE SAMPLE Mix EMWS Commercial (B+D) Lab-grown Algae algae

  8. BIOCHAR PRODUCTION SLOW PYROL YSIS HEATING BIOMASS TYPE TEMPERATURE PROCESS TIME CURVE INITIAL PRODUCT FINAL PRODUCT FINAL PRODUCT CHARACTERIZATI CHARACTERIZATI CHARACTERIZATI ON ON ON Elemental Analysis TGA Analysis Specifjc Surface Elemental Analysis Area Porosity LHV

  9. INITIAL CHARACTERIZATION N - TGA AIR TGA • Humidity content • Humidity Content • Pyrolysis T emperature • Ash Content

  10. INITIAL CHARACTERIZATION SAMPLE A , Mix SAMPLE B , Algae grown in lab SAMPLE C , Commercial SAMPLE D , UMWS Algae

  11. AIR TGA RESULTS SAMPLE ASH CONTENT A, Mix 24 % B, Lab grown Algae 14 % C, Commercial algae 5 % D, UMWS 30 %

  12. PYROLYSIS TESTS

  13. PYROLYSIS PRODUCTS SAMPLE D 500°C, SAMPLE A (MIX) SAMPLE C 500°C, 500°C, Uniform Uniform Varied granulometry, granulometry, black Granulometry, black black SAMPLE A (MIX) 350°C, SAMPLE C 350°C, SAMPLE D 350°C, Uniform granulometry, Varied granulometry, Uniform brown black granulometry, brown 13 Università degli studi di Pavia

  14. PRODUCTS Pyrolysis sample A Pyrolysis sample C 90 90 80 80 500 °C 500 °C 350 °C 350 °C 70 70 60 60 50 50 40 40 30 30 20 20 10 10 0 0 T1 T2 T1 T2 Biochar Bio-olio Gas (stima) Biochar Bio-olio Gas (stima) Pyrolysis sample D 90 80 500 °C 350 °C 70 60 50 40 30 20 10 0 T1 T2 Biochar Bio-olio Gas (stima)

  15. PYROLYSIS PRODUCTS SUMMARY SAMPLE T (°C) % % Bio- % % H 2 O Biochar oil Gas 500 63 15 22 500 62 8 30 1 500 62 13 25 Sample A 5 350 81 4 15 350 85 6 9 2 350 82 7 11 500 50 15 35 500 50 14 36 3 500 52 11 37 Sample C 5 350 82 11 7 350 80 10 10 4 350 72 10 18 500 64 12 24 500 61 18 21 5 500 69 14 17 Sample 9 350 87 12 1 D 350 79 13 8 6 350 80 14 6

  16. BIOCHAR CHARACTERIZATION TEST PURPOSE TGA in air Determine ash content TGA in nitrogen gas Verifjcation of pyrolysis completion IR Chem. Bounds Variation after pyrolysis Calorimetry Determine HCC SAMPLE HCC (MJ/kg) 1 16 2 17 3 17 4 16 5 29 6 27

  17. RESULTS DISCUSSION 1. UMWS PYROL YSIS INITIAL SAMPLE REACTOR T °C GAS REFERENCE WEIGHT (Domı et al., Quarts, 350, 450, UMWS He 30 g 2009) fmuidized bed 550, 950 (Hossain et al., T ubular 300, 400, UMWS Nitrogen 264 – 273 g 2011) fmuidized bed 500, 700 UMWS Sand bed 350, 500 Nitrogen 20 This work (Domı et al., (Hossain et al., This work 2009) 2011) FRACTI ON 350 °C 550 °C 300 °C 550 °C 350 °C 500°C % char 52 49 72.3 57.9 82 65 % oil 10 9 - - 13 15 % gas 20 21 - - 5 20 17

  18. RESULTS DISCUSSION 2. MICROALGAE PYROL YSIS HEATING INITIAL SAMPLE REACTOR T °C GAS REF . RATE WEIGHT Nitroge Chlorella Sand bed 350, 500 5 °C/min 20 g This work n Chlorella- T ubular, 300, nitroge (Chang et al., based fmuidized 400, 10 °C/min 0,2 g n 2015) residuals bed 500, 700 T °C YIELD BIOCHAR (%) 350 78 500 50

  19. DISCUSSION 3. CO-PYROL YSIS OF UMWS and MICROALGAE @ 500 °C @ 350 °C 70 90 80 60 70 50 60 40 50 40 30 30 20 20 10 10 0 0 MIX FANGHI MIX FANGHI Ceneri T ot char Ceneri T ot char

  20. BIOCHAR APPLICATIONS SOIL AMMENDANT INORGANIC & ORGANIC POLLUTANTS ADSORBENT TREATAMENT OF INDUSTRIAL WASTE WATER ANODIC MATERIAL (MFCs) FUEL

  21. CONCLUSIONS  UMWS and algae co-pyrolysis is a sustainable solution to the disposal issue  Production of solid residue with multiple applications  Determination of ideal ratio UMWS/algae to maximise biochar production

  22. THANK YOU!!! … and, remember: save this date https://iwa-network.org/events/15th-iwa-specialist-conference-on-water-basin-and-r iver-management /

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