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Anaerobic digestion of food waste: Effect of autoclave pre-treatment on NH4-N

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Anaerobic digestion of food waste: Effect of autoclave pre-treatment on NH 4 -N

Introduction

Anaerobic digestion of food (FW) waste may be difficult due to the high protein content leading to a high ammonium (NH4-N) concentration during digestion. In this study the effect of autoclaving on the ammonium formation during anaerobic digestion of FW was studied at different organic loading rates (OLRs).

13th World Congress on Anaerobic Digestion 2013, June 25-28, Santiago de Compostela, Spain

Elina Tampio1, Satu Ervasti1, Teija Paavola2, Sonia Heaven3, Charles Banks3, Jukka Rintala1

1MTT Agrifood Research, Finland; 2Biovakka Suomi Ltd, Finland; 3University of Southampton, UK

Materials and methods

11-litre semi-continuously stirred tank reactors, R1 and R2, were operating at 37 ºC. R1 was fed with control FW (NH4-N 0.3 ± 0.1 g kg-1, Total Kjeldahl Nitrogen 7.4 ± 0.3 g kg-1) and R2 with autoclaved FW(160 ºC, 6.2 bar) (NH4-N 0.4 ± 0.1 g kg-1, Total Kjeldahl Nitrogen 6.8 ± 0.3 g kg-1). Both digesters were supplemented with trace element solutions from day 199 onwards (Banks et al. 2012). The OLRs and hydraulic retention times (HRTs) during the study period are presented in Table 1.

The initial inoculum NH4-N concentration was 2.4 g kg-1.

With the autoclaved FW the nitrogen present as proteins was not able to be hydrolysed during the anaerobic digestion. Most likely this was caused by formation of Maillard compounds through reactions between proteins and sugars. These compounds change the biodegradability of the material making it harder or even impossible to degrade, with the result that the simple free and ionic forms of ammonia are not present. The increasing NH4-N in control reactor was as a result of the effective hydrolysis of protein material.

Conclusions

Autoclave treatment of FW decreased NH4-N concentration during anaerobic digestion which may reduce the risk of ammonia inhibition, but will also affect the overall conversion efficiency.

OLR

(kg VSm-3day-1) Days Reactor HRT (d)

2 19-150 R1 117

R2 94

3 151-255 R1 78

R2 63

4 256-417 R1 58

R2 47

6

418-439

R1 39

R2 31

Figure 1. NH4-N and pH during organic loading rates 2, 3, 4 and 6 kgVSm-3day-1 in control (R1) and autoclaved (R2) reactors. OLR increase is presented with

vertical lines.

Table 1. OLRs and HRTs applied to the reactors (R1 control, R2 autoclaved).

References

Banks, C.J., Zhang, Y., Jiang, Y., Heaven, S., 2012. Trace element requirements for stable food waste digestion at elevated ammonia concentrations. Bioresour. Technol.

104, 127-135.

Results and discussion

NH4-N formation during anaerobic digestion was observed to decrease as a result of the autoclave treatment from 2.4 to 1.2 g kg-1 as the OLR was increased from 2 to 6 kg VS m-3 day-1 (Figure 1). In contrast NH4-N in the control reactor increased to 4 g kg-1 over the same OLR increases after which the concentration stabilized at around 3.5 g kg-1. The different NH4-N concentrations affected the pH value and stability of the reactors.

VALORGAS

6.0 6.5 7.0 7.5 8.0

0.0 2.0 4.0 6.0 8.0

0 50 100 150 200 250 300 350 400 450 500

pH

NH4-N (g kg-1)

Days (d)

NH4-N R1 NH4-N R2 pH R1 pH R2

OLR 2 OLR 3 OLR 4 OLR 6

Acknowledgements

This work was funded by by EU FP7 VALORGAS project (241334). The authors are grateful to Aerothermal Group for autoclaving and MTT laboratory staff for their excellent work.

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