Two-phase (acidogenic–methanogenic) anaerobic thermophilic/mesophilic digestion system for producing Class A biosolids from municipal sludge

2010 ◽  
Vol 101 (2) ◽  
pp. 576-585 ◽  
Author(s):  
L.A. Rubio-Loza ◽  
A. Noyola
2006 ◽  
Vol 2006 (2) ◽  
pp. 705-715
Author(s):  
David Bible ◽  
Bob Borneman ◽  
Alice Cannella

2014 ◽  
Vol 5 (1) ◽  
pp. 56-63 ◽  
Author(s):  
Daniel De los Cobos-Vasconcelos ◽  
María Elena Villalba-Pastrana ◽  
Adalberto Noyola

Production of Class A biosolids depends mainly on the effective control of thermotolerant coliforms and Salmonella spp. Thermal pre-treatment followed by anaerobic mesophilic digestion may be a simpler and more sustainable option to accomplish this compared with other process arrangements. In this work, removal and inactivation of thermotolerant coliforms and Salmonella spp. in waste municipal sludge were studied at three thermal pre-treatment conditions in batch tests (60, 70 and 80 °C). Effective removal was obtained with 70 °C and one-hour pre-treatment, but reactivation of both pathogens was noticed in the following step using an anaerobic mesophilic digester. Predictive microbial decay models (Weibull and sigmoidal-empirical) were used for fitting the experimental data. The sigmoidal-empirical model showed better results at the final counts, suggesting thermal adaptation of some microbial subpopulations. In order to overcome this unexpected result, the influence of the cooling phase was also studied applying three different conditions. For effective treatment, a fast cooling step (in this case, an ice-bath with sodium chloride) should follow thermal pre-treatment (70 °C and 60 min). At these conditions, no reactivation or re-growth of both pathogen indicators were seen during the following 48 h under anaerobic mesophilic digestion.


2006 ◽  
Vol 1 (4) ◽  
Author(s):  
Huub H.J. Cox ◽  
Steve Fan ◽  
Reza Iranpour

Terminal Island Treatment Plant converted its digesters to thermophilic operation with the objective to comply with the U.S. EPA Part 503 Biosolids Rule requirements for Class A biosolids. The following processes were tested: a) single-stage continuous; b) two-stage continuous; c) single-stage sequencing batch. Salmonella sp. were always non-detect in digester outflows (<3 MPN/4 g dry wt), whereas fecal coliform densities were usually below the Class A limit of 1000 MPN/g dry wt. However, the recurrence of fecal coliforms in post-digestion caused non-compliance with the Class A limit at the truck loading facility as the last point of plant control for compliance. After several design modifications of the post-digestion train, operation of the digesters as sequencing batch digesters according to the time-temperature requirement of Alternative 1 of the Part 503 Biosolids Rule achieved compliance for both Salmonella sp. and fecal coliforms at the last point of plant control (truck loading facility).


2009 ◽  
Vol 2009 (3) ◽  
pp. 462-478
Author(s):  
Bo Vestergaard-Hansen ◽  
Brigitte McCarty ◽  
Art Molseed ◽  
Travis Smith

2007 ◽  
Vol 2007 (3) ◽  
pp. 498-519
Author(s):  
Greg Moen ◽  
Tom Krueger ◽  
Brad Martin ◽  
Lee Cronister
Keyword(s):  
Class A ◽  

1999 ◽  
Vol 40 (11-12) ◽  
pp. 169-177 ◽  
Author(s):  
S. Ghosh ◽  
D. C. Taylor

Kraft primary and mixed primary-activated sludges were gasified by thermophilic (50 °C) high-rate and mesophilic two-phase digestion. Kraft sludges were deficient in nitrogen, phosphorus, and other unidentified nutrients. Municipal sludge proved to be a much better nutrient source than inorganic salts. Performance of the mesophilic (35°C), two-phase anaerobic digestion (TPAD) system was about the same as that of thermophilic single-stage, high-rate digestion at a 10-day HRT as judged in terms of methane yield (0.17 SCM/kg VS added) and VS reduction efficiency (43%). The mesophilic TPAD process yielded a higher methane-content (65%) fuel gas; it is capable of exhibiting higher net-energy recovery efficiency than thermophilic single-stage digestion.


Sign in / Sign up

Export Citation Format

Share Document