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6 th International Conference on Sustainable Solid Waste Management Study of the Effects of Temperature and pH on Acidogenic Fermentation Process from Organic Fraction of Municipal Solid Waste Y.K. Cheah 1 , C. Vidal-Antich 1 , J. Dosta 1 , J.


  1. 6 th International Conference on Sustainable Solid Waste Management Study of the Effects of Temperature and pH on Acidogenic Fermentation Process from Organic Fraction of Municipal Solid Waste Y.K. Cheah 1 , C. Vidal-Antich 1 , J. Dosta 1 , J. Mata- Á lvarez 1,2 1 Department of Chemical Engineering and Analytical Chemistry, University of Barcelona, Barcelona, Catalonia, 08028, Spain. 2 Water Research Institute, University of Barcelona, Catalonia, 08001, Spain.

  2. Contents 1. Introduction  Waste to resource  OFMSW  Anaerobic digestion 2. Objectives 3. Materials & Methods  Batch test  Continuous reactor 4. Results & Discussions  Effects of temperature  Effects of pH  VFA distribution 5. Conclusions 2

  3. Introduction Waste to resource Source sorted OFMSW VFA Mechanically 3 sorted OFMSW

  4. Introduction OFMSW World Bank, 2012 4

  5. Introduction Anaerobic Digestion Lipid Proteins Carbohydrates Hydrolysis Fatty acids Amino acids Sugars Acidogenesis Intermediate products (VFA: propionic acid, butyric acid…) Acetogenesis Acetic acid CO 2 & H 2 Methanogenesis CH 4 + CO 2 5

  6. Objectives Research goals • To evaluate the VFA production in acidogenic fermentation of OFMSW by manipulating pH and temperature conditions which can be performed in continuous reactors. • To assess the distribution of individual VFA (acetic, propionic, butyric and valeric acids) in the effluent which will be used for PHA production. 6

  7. Materials and Methods Experimental Set-up Batch test OFMSW Inoculum Effects of Temperature (A1) Effects of pH (A2) T = 35, 55, 70 ºC T = 70 ºC Without pH control pH = 3, 4, 5, 8, 9, 10, Period = 6 d 12, without pH control Period = 6 d 7

  8. Materials and Methods Experimental Set-up Continuous OFMSW Inoculum Effects of Temperature Effects of pH B1, B2 B2, B3, B4 T = 35, 70 ºC T = 35, 70 ºC Without pH control pH = 10, without pH control HRT = 3.5 d HRT = 3.5 d 8

  9. Results and Discussions Characterization Source sorted OFMSW from a mechanical-biological treatment plant (Ecoparc) of the Barcelona Metropolitan Area Prefermented OFMSW OFMSW Sampling BIOGAS (from Trommel) ANAEROBIC PREPARATION TANK DIGESTION (Mixer + Shredder) Rejected DIGESTATE solids S/L Purged SEPARATOR Wastewater Characterization of OFMSW Units Value Total Solids (TS) % w/w 6.21 ± 1.29 Volatile Solids (VS) % w/w 4.76 ± 1.13 Soluble Chemical Oxygen Demand (SCOD) g/L 72.53 ± 12.98 Volatile Fatty Acids (VFA) g/L 9.57 ± 1.05 Alkalinity gCaCO 3 /L 4.99 ± 0.51 + ‐ N/L Ammonium ‐ nitrogen concentration gNH 4 2.84 ± 0.66 9 pH ‐ 6.28 ± 0.36

  10. Results and Discussions Effects of temperature Batch Temperature Temperature 35ºC 35ºC 55ºC 55ºC 70ºC 70ºC Sludge from acidogenic Sludge from acidogenic Sludge from acidogenic Inoculum Inoculum fermenter at 35 ºC fermenter at 70 ºC fermenter at 70 ºC Ratio Ra tio 1 1 1 VS feed VS eed /VS /VS slu sludge pH con pH control rol No No No VFA concentration (g/L) 15 10 35 ⁰ C 55 ⁰ C 5 70 ⁰ C 0 1 2 3 4 5 6 Time (d) 10

  11. Results and Discussions Effects of temperature Continuous 25 35 °C 70 °C VFA concentration (g/L) 20 15 10 5 0 0 10 20 30 40 50 60 70 80 Time (d) 11

  12. Results and Discussions Effects of temperature Parameters Units B1 B2 (35 º C, without (70 º C, without pH control) pH control) Alk gCaCO 3 /L 3.01 ± 2.82 7.34 ± 1.42 + ‐ N + ‐ N/L NH 4 gNH 4 3.14 ± 0.10 4.83 ± 0.81 Free ammonia gNH 3 ‐ N/L 0.003 ± 0.000 0.07 ± 0.01 pH ‐ 5.96 ± 0.32 6.17 ± 0.33 sCOD g/L 76.66 ± 12.48 95.10 ± 16.00 VFA COD/sCOD % 22.59 ± 3.78 21.32 ± 4.22 VFA g/L 10.91 ± 1.08 14.59 ± 2.54 Acetic % 38.16 ± 4.21 39.81 ± 2.67 Propionic % 20.93 ± 1.83 21.65 ± 0.91 Butyric % 18.67 ± 2.06 19.19 ± 2.52 Valeric % 10.83 ± 1.27 9.93 ± 0.82 (C 2 +C 4 )/(C 3 +C 5 ) ‐ 1.76 ± 0.23 1.85 ± 0.09 12

  13. Results and Discussions Effects of pH Batch T = 70 ºC; Experiments were carried out in duplicate Inoculum: Sludge from B2 (70 ºC without pH control) pH 3 pH 4 pH 5 pH 8 pH 9 pH 10 pH 12 Blank 16 pH ≥ 10 pH ≥ 10 pH ≥ 10 pH ≥ 10 pH ≥ 10 pH ≥ 10 14 VFA concentration (g/L) pH ≤ 5 pH ≤ 5 pH ≤ 5 pH ≤ 5 pH ≤ 5 pH ≤ 5 12 10 8 6 4 2 0 1 2 3 4 5 6 Time (d) 13

  14. Results and Discussions Effects of pH Continuous Without pH 18 control With pH 16 control VFA concentration (g/L) 14 12 10 8 6 4 2 0 1 2 5 6 7 8 9 12 13 14 16 19 20 21 22 30 Time (d) 14

  15. Results and Discussions VFA distribution Parameters Units B1 B2 B3* B4 (35 º C, without (70 º C, without (70 º C, pH=10) (35 º C, pH=10) pH control) pH control) Alk gCaCO 3 /L 3.01 ± 2.82 7.34 ± 1.42 9.36 ± 0.30 10.10 ± 0.82 + ‐ N + ‐ N/L NH 4 gNH 4 3.14 ± 0.10 4.83 ± 0.81 1.42 ± 0.67 1.97 ± 0.59 Free ammonia gNH 3 ‐ N/L 0.003 ± 0.000 0.07 ± 0.01 1.40 ± 0.66 1.77 ± 0.53 pH ‐ 5.96 ± 0.32 6.17 ± 0.33 9.95 ± 0.18 9.90 ± 0.16 sCOD g/L 95.1 ± 16.0 84.72 ± 15.41 88.21 ± 21.99 76.66 ± 12.48 VFA COD/sCOD % 22.59 ± 3.78 21.32 ± 4.22 19.19 ± 5.07 18.05 ± 3.29 VFA g/L 14.59 ± 2.54 9.85 ± 1.04 10.43 ± 1.13 10.91 ± 1.08 Acetic % 38.16 ± 4.21 39.81 ± 2.67 38.77 ± 1.61 40.08 ± 4.49 Propionic % 20.93 ± 1.83 21.65 ± 0.91 22.10 ± 1.26 20.22 ± 2.07 Butyric % 18.67 ± 2.06 19.19 ± 2.52 16.29 ± 1.89 18.12 ± 3.97 Valeric % 10.83 ± 1.27 9.93 ± 0.82 9.92 ± 0.96 9.86 ± 1.95 (C 2 +C 4 )/(C 3 +C 5 ) ‐ 1.76 ± 0.23 1.85 ± 0.09 1.79 ± 0.09 1.93 ± 0.13 * 30 days of operation 15

  16. Results and Discussions VFA distribution Acetic Propionic Butyric Valeric 50% VFA composition (%) 40% 30% 20% 10% 0% 1 2 5 6 7 8 9 12 13 14 16 19 20 21 22 30 Time (d) 16

  17. Conclusions Conclusive remarks  Collected OFMSW was prefermented at pH 6.2 and the distribution of VFA was even suitable for PHA production.  Without pH control, the hyperthermophilic range at 70 ºC is more favourable for maximum VFA production.  Generally, the composition of individual VFA in all reactors were similar to that of influent (OFMSW from Ecoparc).  Fermenters at 35 ºC and 70 ºC working at pH 10 did not produce a higher VFA quantity than the fermenters working at acidic pH, probably due to the free ammonia inhibition . � � �� �  Effluents from the fermenters has a proportion � � �� � ≈ 1.8; ��� ��� ��� � ≈ 18-22 % and high NH 4 + -N ≥ 1.4 g/L. 17

  18. Acknowledgement Thank you for your attention 18

  19. 6 th International Conference on Sustainable Solid Waste Management Study of the Effects of Temperature and pH on Acidogenic Fermentation Process from Organic Fraction of Municipal Solid Waste Y.K. Cheah 1 , C. Vidal-Antich 1 , J. Dosta 1 , J. Mata- Á lvarez 1,2 1 Department of Chemical Engineering and Analytical Chemistry, University of Barcelona, Barcelona, Catalonia, 08028, Spain. 2 Water Research Institute, University of Barcelona, Catalonia, 08001, Spain.

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