Process for enhanced anaerobic digestion of sludge by alcoholization of food waste

Patent metadata

Field	Value
Publication number	US-11453607-B2
Application number	US-202017101612-A
Country	US
Kind code	B2
Filing date	Nov 23, 2020
Priority date	Aug 31, 2020
Publication date	Sep 27, 2022
Grant date	Sep 27, 2022

Abstract

A process for enhanced anaerobic digestion of sludge by alcoholization of food waste, comprising steps of: (1) ethanol prefermentation of food waste—feeding the food waste having been crushed into a uniform grain size into an ethanol production reactor, where the food waste is subjected to rapid and efficient anaerobic fermentation activated by addition of yeast and pH adjustment to produce ethanol and obtain a fermentation broth and a fermentation residue; (2) sludge pretreatment—pretreating the sludge after mixing with the fermentation residue; and (3) methanogenesis of anaerobic digestion—subjecting products resulting from the sludge pretreatment to be mixed with the fermentation broth and then to methanogenesis of anaerobic digestion in a methane production reactor. With this process, the sludge and the food waste can be treated efficiently via multi-phase reactions, and the resource recovery and biogas quality can be enhanced.

First claim

What is claimed is:

1. A process for enhanced anaerobic digestion of sludge by alcoholization of food waste, comprising steps of:
(1) ethanol prefermentation of food waste—feeding the food waste having been crushed into a uniform grain size into an ethanol production reactor, where the food waste is subjected to anaerobic fermentation activated by addition of yeast and pH adjustment to produce ethanol and obtain a fermentation broth and a fermentation residue;
(2) pretreatment of sludge—feeding the sludge into a pretreatment reactor after mixing with the fermentation residue obtained in the step (1) for pretreatment so that dissolution and degradation properties of organic matter contained in the sludge and in the fermentation residue are improved; and
(3) methanogenesis of anaerobic digestion—subjecting products resulting from the step (2) to be mixed with the fermentation broth obtained in the step (1) and then to methanogenesis of anaerobic digestion in a methane production reactor.

2. The process according to claim 1 , wherein, in the step (1), the food waste is crushed into a grain size smaller than 10 mm before being subjected to the ethanol prefermentation, and mixed thoroughly; and, wherein, the yeast added is Saccharomyces cerevisae , and is inoculated into the food waste in the ethanol production reactor via a portion of the fermentation broth resulting from the ethanol production in a circular manner; and, wherein, the food waste in the ethanol production reactor is adjusted to a pH in the range of from 3.5 to 6.5 with a returned portion of the fermentation broth.

3. The process according to claim 1 , wherein, in the step (1), the ethanol prefermentation of the food waste is carried out at 20 to 30° C. for 4 to 48 hours.

4. The process according to claim 1 , wherein, in the step (2), a ratio of a total solids content in the fermentation residue of the food waste to a total solids content in the sludge is 10 to 0.1.

5. The process according to claim 1 , wherein, the sludge in the step (2) is at least one of: primary sludge, secondary sludge, excess activated sludge, concentrated sludge, and dehydrated sludge from a sewage treatment plant; and, wherein, the pretreatment of the sludge comprises at least one of enzyme, ozone, ultrasonic, microwave treatments, and thermal hydrolysis.

6. The process according to claim 1 , wherein, the methanogenesis in the step (3) is carried out with stirring at a stirring speed of 60 to 120 rpm for 10 to 30 days.

7. The process according to claim 1 , wherein, the methanogenesis in the step (3) is carried out at a medium temperature of 30 to 40° C., or at a high temperature of 50 to 60° C., or at a medium high temperature of 40 to 50° C.; and, wherein, the mixture of the products resulting from the sludge pretreatment and the fermentation broth of the food waste has a total solid content within a low range of 2 to 10% or within a high range of 15 to 35%.

8. The process according to claim 1 , wherein, in the step (3), an iron-based or carbon-based conductive material or an iron-carbon composite conductive material is added to the methane production reactor.

9. The process according to claim 8 , wherein, the iron-based material comprises at least one of: magnetite, hematite, and goethite; and, wherein, the carbon-based material comprises at least one of: biochar, activated carbon, graphites, graphene, carbon cloth, and carbon nanotubes.

10. The process according to claim 1 , wherein, in the step (3), the methane production reactor is coupled to an electrochemical device which is configured for applying a voltage within the range of 0.1 to 3.0 volts to a methanogenic phase.

Assignees

• Univ Tongji

Inventors

• Dai Xiaohu
• Li Lei
• Gao Jun
• Xu Ying
• Dong Bin
• Dai Lingling
• Liu Zhigang

Classifications

• C02F2203/00

  Apparatus and plants for the biological treatment of water, waste water or sewage · CPC title

• C02F3/005

  Combined electrochemical biological processes (aeration by electrolytically produced oxygen bubbles C02F3/202) · CPC title

• C02F2303/06

  Sludge reduction, e.g. by lysis · CPC title

• C02F1/302

  with microwaves · CPC title

• C02F2303/26

  Reducing the size of particles, liquid droplets or bubbles, e.g. by crushing, grinding, spraying, creation of microbubbles or nanobubbles · CPC title