Literature DB >> 17197176

Propionic acid accumulation and degradation during restart of a full-scale anaerobic biowaste digester.

C Gallert1, J Winter.   

Abstract

The methane formation rate of 300 m(3) of sludge from a full scale biowaste reactor, that was stored without feeding for six weeks during a maintenance period, was about 60% of the methanogenic activity before maintenance. The 300 m(3) sludge was then pumped back into the biowaste reactor. On the third day, after refilling of the stored biowaste suspension, anaerobic conditions were obtained and feeding was started by addition of 36.1 m(3) of fresh biowaste suspension (=11.3 tons biowaste). The pH dropped from originally pH 7.7 to pH 7.3 and later on to pH 6.8, which was considered the minimum allowed pH for methanogenesis to recover. Maximum concentrations of acetate (1.78 gl(-1)), n-butyrate (0.57 gl(-1)) and n-valerate (0.44 gl(-1)) accumulated during the following days with feeding of 11.8 tons on day 5 and twice 6.5 tons on days 7 and 9, respectively. Thereafter, acetate, n-butyrate and n-valerate were degraded completely, whereas the concentration of propionate was still increasing. Propionic acid was the dominant fatty acid during the restart period and reached its maximum concentration of 6.2 gl(-1) 17 days after start of feeding. This high level of propionate was degraded completely in about 5 days with maximum degradation rates of 2.14 gl(-1)d(-1), and the pH of the anaerobic sludge increased from 7.1 to 7.4. During restart, the methane content of the biogas increased successively to 65%. Samples that were taken at different time intervals during the restart phase of the methane reactor showed different fatty acid degradation capabilities. After 10 days, when acetate and n-butyrate still accumulated in the methane reactor the maximum acetate degradation rate was 1.52 gl(-1)d(-1) and the n-butyrate degradation rate was 0.51 gl(-1)d(-1). Oxidation of n-valerate caused an increase of propionate, which was degraded after a lag phase of 6 days with a maximum rate of 0.6 gl(-1)d(-1). In the samples taken after 16 and 23 days, the propionate degradation rate increased to 1.42 gl(-1)d(-1) and 1.55 gl(-1)d(-1), respectively, and the lag phase for propionate degradation was reduced or had disappeared completely. The maximum propionate degradation rate was measured in the methane reactor in the fourth week after restart. The synthrophic propionate oxidizing bacteria were apparently the most suffering bacteria during sludge storage. If the propionate oxidizing bacteria could be kept active and the propionate degrading activity of the biowaste suspension of 6.16 gl(-1)d(-1) before the maintenance period could be maintained, then accumulation of 6.2 gl(-1) propionate in the methane reactor after restart could be avoided and full activity reached even earlier.

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Year:  2007        PMID: 17197176     DOI: 10.1016/j.biortech.2006.11.014

Source DB:  PubMed          Journal:  Bioresour Technol        ISSN: 0960-8524            Impact factor:   9.642


  11 in total

1.  Syntrophic propionate oxidation via butyrate: a novel window of opportunity under methanogenic conditions.

Authors:  Jan Dolfing
Journal:  Appl Environ Microbiol       Date:  2013-07       Impact factor: 4.792

2.  Mediative mechanism of bicarbonate on anaerobic propionate degradation revealed by microbial community and thermodynamics.

Authors:  Yupeng Zhang; Jianzheng Li; Fengqin Liu; Han Yan; Jiuling Li
Journal:  Environ Sci Pollut Res Int       Date:  2018-02-19       Impact factor: 4.223

Review 3.  Syntrophic propionate-oxidizing bacteria in methanogenic systems.

Authors:  Maria Westerholm; Magdalena Calusinska; Jan Dolfing
Journal:  FEMS Microbiol Rev       Date:  2022-03-03       Impact factor: 16.408

4.  Bioclogging in porous media: influence in reduction of hydraulic conductivity and organic contaminants during synthetic leachate permeation.

Authors:  Subramaniam Kanmani; Rajan Gandhimathi; Kasinathan Muthukkumaran
Journal:  J Environ Health Sci Eng       Date:  2014-10-29

5.  A metagenomic study of the microbial communities in four parallel biogas reactors.

Authors:  Linn Solli; Othilde Elise Håvelsrud; Svein Jarle Horn; Anne Gunn Rike
Journal:  Biotechnol Biofuels       Date:  2014-10-14       Impact factor: 6.040

6.  Microbial Community Shifts during Biogas Production from Biowaste and/or Propionate.

Authors:  Chaoran Li; Christoph Moertelmaier; Josef Winter; Claudia Gallert
Journal:  Bioengineering (Basel)       Date:  2015-02-09

7.  Temporal Microbial Community Dynamics in Microbial Electrolysis Cells - Influence of Acetate and Propionate Concentration.

Authors:  Ananda Rao Hari; Krishnaveni Venkidusamy; Krishna P Katuri; Samik Bagchi; Pascal E Saikaly
Journal:  Front Microbiol       Date:  2017-07-20       Impact factor: 5.640

8.  Set anode potentials affect the electron fluxes and microbial community structure in propionate-fed microbial electrolysis cells.

Authors:  Ananda Rao Hari; Krishna P Katuri; Bruce E Logan; Pascal E Saikaly
Journal:  Sci Rep       Date:  2016-12-09       Impact factor: 4.379

9.  Biodiversity-function relationships in methanogenic communities.

Authors:  Pawel Sierocinski; Florian Bayer; Gabriel Yvon-Durocher; Melia Burdon; Tobias Großkopf; Mark Alston; David Swarbreck; Phil J Hobbs; Orkun S Soyer; Angus Buckling
Journal:  Mol Ecol       Date:  2018-11-22       Impact factor: 6.185

10.  Control of accumulated volatile fatty acids by recycling nitrified effluent.

Authors:  Jun-Gyu Park; Beom Lee; Sang-Yeol Jo; Jun-Sang Lee; Hang-Bae Jun
Journal:  J Environ Health Sci Eng       Date:  2018-03-29
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