Abstract

Anaerobic sludge stabilization is a commonly used technology. Most fermenters are operated at a mesophilic temperature regime. Modern trends in waste management aim to minimize waste generation. One of the strategies can be achieved by anaerobically stabilizing the sludge by raising the temperature. Higher temperatures will allow faster decomposition of organic matter, shortening the retention time, and increasing biogas production. This work is focused on the description of changes in the community of methanogenic microorganisms at different temperatures during the sludge stabilization. At higher temperatures, biogas contained a higher percentage of methane, however, there was an undesirable accumulation of ammonia in the fermenter. Representatives of the hydrogenotrophic genus Methanoliea were described at all temperatures tested. At temperatures up to 50 °C, a significant proportion of methanogens were also formed by acetoclastic representatives of Methanosaeta sp. and acetoclastic representatives of the order Methanosarcinales. The composition of methanogens in the fermenter significantly changed at 60 °C when typically thermophilic species, like Methanothermobacter marburgensis, appeared. A decrease in the diversity of methanogens was observed, and typical hydrogenotrophic methanogenic archaea isolated from fermenters of biogas plants and anaerobic wastewater treatment plants represented by genus Methanoculleus were no longer present.

Highlights

  • Wastewater treatment is an important process ensuring sustainable development of human society.On average, 144 L of water per person per day is supplied by households in Europe [1]

  • The results show the dependency between the temperatures and organic dry matter content degradation (Figure 2a)

  • The results show the dependency between the temperatures and organic5 dry of 12 matter content degradation (Figure 2a)

Read more

Summary

Introduction

Wastewater treatment is an important process ensuring sustainable development of human society. 144 L of water per person per day is supplied by households in Europe [1]. Most of this water, along with the water from the industry, will become wastewater after use. Along with the water from the industry, will become wastewater after use This water is discharged to wastewater treatment plants (WWTPs). In the process of wastewater treatment to purified water, we get other products that we need to handle, as gravel, sand, screenings and sewage sludge. Gravel and sand are usually landfilled, incinerated, used for reclamation or construction purposes

Methods
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call