Abstract

This study investigated the effects of initiating anaerobic digestion (AD) of dry layer-hen poultry dung at the sub-atmospheric pressure of -30 cmHg on biodegradation, biogasification, and biomethanation. The setup was performed as a batch process at an average ambient temperature of 29±2 0 C and a retention time of 15 days. Comparisons were made with two other experiments which were both begun at ambient atmospheric pressure; one was inoculated with digestate from a previous layer-hen dung AD, while the other was not inoculated. The bioreactors initiated at sub-atmospheric pressure, ambient atmospheric pressure without inoculum, and ambient atmospheric pressure with inoculum showed the following for biogas and biomethane yields respectively: 16.8 cm 3 g -1 VS and 15.46 cm 3 g -1 VS, 25.10 cm 3 g -1 VS and 12.85 cm 3 g -1 VS, 21.44 cm 3 g -1 VS and 14.88 cm 3 g - 1 VS. In the same order, after AD, the following values were recorded for volatile solids and total viable counts (prokaryotes and fungi) in the digestates: 40.33% and 23.22 x 10 6 cfu mL -1 , 43.42% and 22.17 x 10 6 cfu mL -1 , 41.11% and 13.3 x 10 6 cfu mL -1 . The feedstock showed values of 83.93% and 3.98 x 10 6 cfu mL -1 for volatile solids and total viable count respectively. There was a slight difference in the volatile solids of the digestates of the three bioreactors after AD. The pH recorded for the feedstock slurry before AD was 7.9 at 30 o C, while after AD, the digestates from all the three bioreactors showed the same pH of 5.9 at 29 0 C. Statistical analysis using ANOVA showed no significant difference in biogas yields of the feedstock for the three bioreactors (A, B, C). ANOVA showed no significant difference for biomethane yields in the bioreactors initiated at sub-atmospheric pressure and for those initiated at ambient atmospheric pressure with inoculums. However, it showed significant difference in the bioreactor initiated at sub-atmospheric pressure and that initiated at ambient atmospheric pressure without inoculums, and significant difference in the two sets of bioreactors initiated at ambient atmospheric pressure (with and without inoculum). Initiating AD at reduced atmospheric pressure (-30 cmHg) and the addition of inoculum at ambient atmospheric pressure both increased biomethanation, by 20.31% and 15.80% respectively. The AD initiated at sub-atmospheric pressure yielded the least amount of carbon dioxide (a greenhouse gas), and improved biodegradation and biomethanation. The results also suggest that biomethane production is dependent on specific methanogenic growth. Analyzing the populations of methanogens isolated from the different bioreactors in relation to their biomethane yields suggests that Methanosarcina barkeri may have been largely responsible for the differences in biomethane yields.

Highlights

  • Anaerobic digestion (AD) is a widely accepted method of organic waste management due to its high performance in volume reduction, product stabilization, and production of valuable resources, which makes the process profitable

  • Though the highest biogas yield was seen in the bioreactor initiated at ambient atmospheric pressure, it recorded the least biomethane content; while the bioreactor initiated at sub-atmospheric pressure yielded the lowest biogas volume, but had the highest biomethane content

  • ANOVA revealed that statistically there was no significant difference in biogas yields; there were significant differences in biomethane yields between the bioreactor initiated at sub-atmospheric pressure and that initiated at ambient atmospheric pressure without inoculum, and between the two bioreactors initiated at ambient atmospheric pressure

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Summary

Introduction

Anaerobic digestion (AD) is a widely accepted method of organic waste management due to its high performance in volume reduction, product stabilization, and production of valuable resources (biogas and biofertilizer), which makes the process profitable. Ultrasonic treatment has been reported by Tiehm et al (2001) and Bougrier et al (2005) to increase digestibility through a size reduction of the organic waste particulate matter. It has been reported that the efficiency of the AD process is influenced by environmental and operational parameters (treatment), such as: temperature, nutrient availability, light, oxygen levels, pH, presence of inhibitors, and so on (Monnet, 2003). Skillfully manipulating these parameters, singularly or in combination, may lead to an improvement in the overall efficiency of the process (Schnurer and Jarvis, 2010). The reasons given were that the removal of produced biogas can increase the attainable microbial population (this can be up to a factor of 12 in the case of extremely thermophilic methanogens), and the removal of gases, for example hydrogen sulfide and ammonia, which may inhibit methanogenesis (Deublein and Steinhauser, 2008)

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