Abstract

Abstract. The effect of temperature on bio-hydrogen production by co-digestion of sewerage sludge with food waste and its two derivatives, i.e. noodle waste and rice waste, was investigated by statistical modelling. Experimental results showed that increasing temperature from mesophilic (37 °C) to thermophilic (55 °C) was an effective mean for increasing bio-hydrogen production from food waste and noodle waste, but it caused a negative impact on bio-hydrogen production from rice waste. The maximum cumulative bio-hydrogen production of 650 mL was obtained from noodle waste under thermophilic temperature condition. Most of the production was observed during the first 48 h of incubation, which continued until 72 h of incubation. The decline in pH during this interval was 4.3 and 4.4 from a starting value of 7 under mesophilic and thermophilic conditions, respectively. Most of the glucose consumption was also observed during 72 h of incubation and the maximum consumption was observed during the first 24 h, which was the same duration where the maximum pH drop occurred. The maximum hydrogen yields of 82.47 mL VS−1, 131.38 mL COD−1, and 44.90 mL glucose−1 were obtained from thermophilic food waste, thermophilic noodle waste and mesophilic rice waste, respectively. The production of volatile fatty acids increased with an increase in time and temperature in food waste and noodle waste reactors whereas they decreased with temperature in rice waste reactors. The statistical modelling returned good results with high values of coefficient of determination (R2) for each waste type and 3-D response surface plots developed by using models developed. These plots developed a better understanding regarding the impact of temperature and incubation time on bio-hydrogen production trend, glucose consumption during incubation and volatile fatty acids production.

Highlights

  • Anaerobic digestion, as a waste management approach, has been in practice for more than a century (McCarty, 1981)

  • A comparison of actual and Modified Gompertz equation (MGE) modelled bio-hydrogen production under mesophilic and thermophilic conditions is shown in Fig. 1, which shows an early start of bio-hydrogen production in food waste and noodle waste as compared to rice waste

  • The bio-hydrogen production in food waste continued until 72 h of incubation and this time period for food waste was higher than that observed for noodle waste, but still the cumulative bio-hydrogen production of food waste was the lowest as compared to the other two waste types

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Summary

Introduction

Anaerobic digestion , as a waste management approach, has been in practice for more than a century (McCarty, 1981). It is widely used to treat a variety of solid wastes and wastewater on a small scale as well as on an industrial scale. It has multiple advantages like 30–50 % reduction in waste volume as well as production of valuable byproducts such as methane and hydrogen (Lin et al, 2011). The food waste contains more than 80 % volatile solids (VS) that are biodegradable solids and can be converted into hydrogen or methane (Shin et al, 2004; Zhang et al, 2007; Zhu et al, 2008). Several studies represent an increase in bio-hydrogen production from food waste due to the addition of buffers and minerals.

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