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COMPARISON BETWEEN UP- AND DOWNFLOW ANAEROBIC FIXED FILM REACTORS OF VARYING SURFACE-TO-VOLUME RATIOS FOR THE TREATMENT OF BEAN BLANCHING WASTE L. Van Den Berg, Senior Research Officer C. P. Lentz, Principal Research Officer Division of Biological Sciences National Research Council of Canada Ottawa, Canada K1A 0R6 INTRODUCTION The need for greater efficiency and economy in the treatment of industrial and municipal liquid wastes and interest in methane production from biomass as a renewable source of energy has led to renewed interest in anaerobic digestion and the study of new types of fermenters. These new types have in common the retention of active microbial biomass in the fermenters, instead of allowing it to escape with the treated effluent. Included in these types are the anaerobic contact process [1-5], the anaerobic filter (upflow) [6-9], and upflow [10,11] and "plug" flow [12] reactors with indication of fluidized or expanded bed operation. The anaerobic filter, a tower filled with small stones, rings, or other types of filter media through which the waste to be treated flowed upward, was thought to be characterized by an active microbial film attached to the filter medium. There is now indication that much of the active microbial mass is retained in the void spaces in the medium in particles, masses, or clumps, perhaps being tumbled or rolled by the movement of the passing fluid. This tumbling or rolling action is related to the fluidized or expanded bed concept [7,9,10-12]. An actual fixed film reactor would also be a logical development but until now it does not appear to have been studied. A fixed film reactor has a number of advantages over other types of fermenters designed to retain the active microbial biomass in the fermenter. It obviates mixing, difficult to provide for adequately in large tanks, and settling, a major problem with the anaerobic contact process. It can be designed to avoid channelling, a problem inherent in upflow filters, and possibly in other upflow reactors. Also, with the bacteria adhering to a surface, the reactor height is not limited as it appears to be with the anaerobic filter or other upflow reactors. A fixed film reactor may be conceived using a variety of forms of surface to support the adhering film, but in this first study of which we report preliminary results vertical glass tubes or columns were used as fermenters to provide simplicity in predicting active surface area and volume, as well as pattern of flow. Bean blanching waste supplied by a commercial canning company (Canadian Canners Ltd., Burlington, Ontario) was used as substrate. Factors studied during the first year were diameter (hence, surface-to-volume ratio) and direction of flow (up or down), as well as the relation between performance and the length of time columns had been in operation. Performance was mainly based on removal of chemical oxygen demand and of volatile solids and rates of methane production. Observations on the distribution of microbial activity between surface and bulk of liquid were also made. Results obtained were compared with those obtained earlier for bean blanching waste using the anaerobic contact process [3,4]. EXPERIMENTAL Reactors used and their operation are sketched in Figure 1. In downflow reactors, feed (bean blanching waste, 1% total solids, Table I) was pumped in at the top of the reactor together with liquid recirculated from the bottom of the reactor. Effluent was removed from the bottom of the reactor through a level control device. Gas was removed at the top. In upflow reactors feed was pumped in at the bottom, together with recir- 319
Object Description
Purdue Identification Number | ETRIWC197931 |
Title | Comparison between up- and downflow anaerobic fixed film reactors of varying surface-to-volume ratios for the treatment of bean blanching waste |
Author |
Van Den Berg, Lowell A. Lentz, C. P. |
Date of Original | 1979 |
Conference Title | Proceedings of the 34th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,30453 |
Extent of Original | p. 319-325 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University LIbraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Date Digitized | 2009-06-24 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page0319 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | COMPARISON BETWEEN UP- AND DOWNFLOW ANAEROBIC FIXED FILM REACTORS OF VARYING SURFACE-TO-VOLUME RATIOS FOR THE TREATMENT OF BEAN BLANCHING WASTE L. Van Den Berg, Senior Research Officer C. P. Lentz, Principal Research Officer Division of Biological Sciences National Research Council of Canada Ottawa, Canada K1A 0R6 INTRODUCTION The need for greater efficiency and economy in the treatment of industrial and municipal liquid wastes and interest in methane production from biomass as a renewable source of energy has led to renewed interest in anaerobic digestion and the study of new types of fermenters. These new types have in common the retention of active microbial biomass in the fermenters, instead of allowing it to escape with the treated effluent. Included in these types are the anaerobic contact process [1-5], the anaerobic filter (upflow) [6-9], and upflow [10,11] and "plug" flow [12] reactors with indication of fluidized or expanded bed operation. The anaerobic filter, a tower filled with small stones, rings, or other types of filter media through which the waste to be treated flowed upward, was thought to be characterized by an active microbial film attached to the filter medium. There is now indication that much of the active microbial mass is retained in the void spaces in the medium in particles, masses, or clumps, perhaps being tumbled or rolled by the movement of the passing fluid. This tumbling or rolling action is related to the fluidized or expanded bed concept [7,9,10-12]. An actual fixed film reactor would also be a logical development but until now it does not appear to have been studied. A fixed film reactor has a number of advantages over other types of fermenters designed to retain the active microbial biomass in the fermenter. It obviates mixing, difficult to provide for adequately in large tanks, and settling, a major problem with the anaerobic contact process. It can be designed to avoid channelling, a problem inherent in upflow filters, and possibly in other upflow reactors. Also, with the bacteria adhering to a surface, the reactor height is not limited as it appears to be with the anaerobic filter or other upflow reactors. A fixed film reactor may be conceived using a variety of forms of surface to support the adhering film, but in this first study of which we report preliminary results vertical glass tubes or columns were used as fermenters to provide simplicity in predicting active surface area and volume, as well as pattern of flow. Bean blanching waste supplied by a commercial canning company (Canadian Canners Ltd., Burlington, Ontario) was used as substrate. Factors studied during the first year were diameter (hence, surface-to-volume ratio) and direction of flow (up or down), as well as the relation between performance and the length of time columns had been in operation. Performance was mainly based on removal of chemical oxygen demand and of volatile solids and rates of methane production. Observations on the distribution of microbial activity between surface and bulk of liquid were also made. Results obtained were compared with those obtained earlier for bean blanching waste using the anaerobic contact process [3,4]. EXPERIMENTAL Reactors used and their operation are sketched in Figure 1. In downflow reactors, feed (bean blanching waste, 1% total solids, Table I) was pumped in at the top of the reactor together with liquid recirculated from the bottom of the reactor. Effluent was removed from the bottom of the reactor through a level control device. Gas was removed at the top. In upflow reactors feed was pumped in at the bottom, together with recir- 319 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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