Yves Comeau
École Polytechnique de Montréal
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Water Research | 1986
Yves Comeau; Ken J. Hall; R.E.W. Hancock; W.K. Oldham
Abstract Enhanced biological phosphorus (bio-P) removal from wastewater is a promising technology for which the fundamental mechanisms are still unclear. The purpose of this paper is to present a biochemical model that explains bio-P removal mechanisms occurring under anaerobic, aerobic and anoxic conditions of the process. A bio-P bacterium is referred to as one that can store both polyphosphate and carbon (as poly-β-hydroxybutyrate for example). In this communication, observations from the literature are first reviewed and mechanisms of bacterial bioenergetics and membrane transport are summarized. The model for bio-P metabolism under anaerobic, aerobic and anoxic conditions is then presented. The role of polyphosphate under anaerobic conditions is suggested to be as a source of energy both for the reestablishment of the proton motive force, which would be consumed by substrate transport and for substrate storage. The role of the anaerobic zone is to maximize the storage of organic substrates in bio-P bacteria. For this purpose the supply of readily available substrates should be maximized and the presence of electron acceptors (molecular oxygen or oxidized nitrogen) minimized. Under subsequent aerobic or anoxic conditions, bio-P bacteria will accumulate polyphosphates in response to the availability of electron acceptors (oxygen or oxidized nitrogen) for energy production. Carbon reserves in bio-P bacteria should provide energy for growth and for soluble phosphate accumulation as polyphosphate reserves.
Journal of Bacteriology | 2001
Eric Déziel; Yves Comeau; Richard Villemur
Pseudomonas aeruginosa is a ubiquitous environmental bacterium capable of forming biofilms on surfaces as a survival strategy. It exhibits a large variety of competition/virulence factors, such as three types of motilities: flagellum-mediated swimming, flagellum-mediated swarming, and type IV pilus-mediated twitching. A strategy frequently used by bacteria to survive changing environmental conditions is to create a phenotypically heterogeneous population by a mechanism called phase variation. In this report, we describe the characterization of phenotypic variants forming small, rough colonies that spontaneously emerged when P. aeruginosa 57RP was cultivated as a biofilm or in static liquid cultures. These small-colony (S) variants produced abundant type IV fimbriae, displayed defective swimming, swarming, and twitching motilities, and were impaired in chemotaxis. They also autoaggregated in liquid cultures and rapidly initiated the formation of strongly adherent biofilms. In contrast, the large-colony variant (parent form) was poorly adherent, homogeneously dispersed in liquid cultures, and produced scant polar fimbriae. Further analysis of the S variants demonstrated differences in a variety of other phenotypic traits, including increased production of pyocyanin and pyoverdine and reduced elastase activity. Under appropriate growth conditions, cells of each phenotype switched to the other phenotype at a fairly high frequency. We conclude that these S variants resulted from phase variation and were selectively enriched when P. aeruginosa 57RP was grown as a biofilm or in static liquid cultures. We propose that phase variation ensures the prior presence of phenotypic forms well adapted to initiate the formation of a biofilm as soon as environmental conditions are favorable.
Biodegradation | 1999
Eric Déziel; Yves Comeau; Richard Villemur
Two-liquid-phase culture systems involve the addition of a water-immiscible, biocompatible and non-biodegradable solvent to enhance a biocatalytic process. Two-liquid-phase bioreactors have been used since the mid-seventies for the microbial and enzymatic bioconversion of hydrophobic/toxic substrates into products of commercial interest. The increasing popularity of bioremediation technologies suggests a new area of application for this type of bioreactor. The toxicity and the limited bioavailability of many pollutants are important obstacles that must first be overcome in order to improve biodegradation processes. Two-liquid-phase bioreactors have the potential to resolve both limitations of biotreatment technologies by the enhancement of the mass-transfer rate of compounds with low bioavailability, and by the controlled delivery of apolar toxic compounds. This technology can also be useful in accelerating the enrichment of microorganisms degrading problematic pollutants. In this paper, we discuss the application of two-liquid-phase bioreactors to enhance the biodegradation of toxic/poorly bioavailable contaminants. Important microbial mechanisms involved in this type of system are described. Uptake of the substrates can be achieved by microorganisms freely dispersed in the aqueous phase and/or bound at the interface between the aqueous and the immiscible phases. Production of surface-active compounds and adhesion abilities are microbial features involved in the process. General guidelines for the design of two-liquid-phase bioreactors for biodegradation purposes are presented. Solvent selection should be established on specific criteria, which depend on the characteristics of target compound(s) and the microorganism(s) implicated in the biodegradation process. The central importance of maximizing the interfacial surface area is highlighted. The potential of this approach as an alternative to current biotreatment technologies is also discussed.
Applied Microbiology and Biotechnology | 1997
C. Barbeau; Louise Deschênes; Dimitre G. Karamanev; Yves Comeau; Réjean Samson
Abstract The use of an indigenous microbial consortium, pollutant-acclimated and attached to soil particles (activated soil), was studied as a bioaugmentation method for the aerobic biodegradation of pentachlorophenol (PCP) in a contaminated soil. A 125-l completely mixed soil slurry (10% soil) bioreactor was used to produce the activated soil biomass. Results showed that the bioreactor was very effective in producing a PCP-acclimated biomass. Within 30 days, PCP-degrading bacteria increased from 105 cfu/g to 108 cfu/g soil. Mineralization of the PCP added to the reactor was demonstrated by chloride accumulation in solution. The soil-attached consortium produced in the reactor was inhibited by PCP concentrations exceeding 250 mg/l. This high level of tolerance was attributed to the beneficial effect of the soil particles. Once produced, the activated soil biomass remained active for 5 weeks at 20 °C and for up to 3 months when kept at 4 °C. The activated attached soil biomass produced in the completely mixed soil slurry bioreactor, as well as a PCP-acclimated flocculent biomass obtained from an air-lift immobilized-soil bioreactor, were used to stimulate the bioremediation of a PCP-impacted sandy soil, which had no indigenous PCP-degrading microorganisms. Bioaugmentation of this soil by the acclimated biomass resulted in a 99% reduction (from 400 mg/kg to 5 mg/kg in 130 days) in PCP concentration. The PCP degradation rates obtained with the activated soil biomass, produced either as a biomass attached to soil particles or as a flocculent biomass, were similar.
Biological Phosphate Removal from Wastewaters#R##N#Proceedings of an IAWPRC Specialized Conference held in Rome, Italy, 28–30 September, 1987 | 1987
Yves Comeau; W.K. Oldham; Ken J. Hall
ABSTRACT A series of batch tests were conducted to investigate the effects of short chain fatty acids (SCFAs) on carbon storage and consumption involved in the biological dephosphatation of wastewater. Nitrate and nitrite were tested as alternatives to oxygen to assess the importance of denitrifying microorganisms in the phosphorus removal process. Both poly-β-hydroxybutyrate (PHB) and poly-β-hydroxyvalerate (PHV) were stored as carbon reserve material under anaerobic conditions, and consumed under aerobic conditions. The proportion of carbon storage as PHB was larger than that as PHV with the addition of SCFAs containing an even number of carbons (acetate, butyrate), whereas the proportion of PHV was larger when SCFAs with an odd number of carbons were added (propionate, lactate, valerate). Maximum PHV accumulation was reported with combined acetate and propionate addition. With the dephosphating sludge studied, acetate and propionate were the two most “readily stored” carbon substrates. Under aerobic conditions, phosphate uptake, PHB and PHV consumption were reported. Nitrate, but not nitrite, was found to have a similar effect to oxygen. A classification of microbial activity in a dephosphating biomass was presented. It was proposed that PHA storage plays a central role in biological dephosphatation and that the function of the anaerobic zone is to maximize carbon storage in dephosphating bacteria in order to subsequently maximize phosphate uptake under aerobic conditions.
Environmental Technology | 1988
G.J.F.M. Vlekke; Yves Comeau; W.K. Oldham
Abstract The objective of this research was to test the feasibility of using nitrate as sole electron acceptor for biological phosphate removal from wastewater. Two sequencing batch reactors, one with nitrate and the other one with air to supply oxygen, were used to develop two sets of acclimated biomass. It was shown that it was possible to induce biological phosphate removal with nitrate alone, confirming the ability of denitrifying bacteria for this process. A preliminary comparison, however, suggested that nitrate may be less efficient than oxygen for phosphate uptake.
Biotechnology Progress | 2000
Richard Villemur; Eric Déziel; Amine Benachenhou; José Marcoux; Emilie Gauthier; François Lépine; Réjean Beaudet; Yves Comeau
High‐molecular‐weight (HMW) polycyclic aromatic hydrocarbons (PAHs) are pollutants that persist in the environment due to their low solubility in water and their sequestration by soil and sediments. The addition of a water‐immiscible, nonbiodegradable, and biocompatible liquid, silicone oil, to a soil slurry was studied to promote the desorption of PAHs from soil and to increase their bioavailability. First, the transfer into silicone oil of phenanthrene, pyrene, chrysene, and benzo[a]pyrene added to a sterilized soil (sandy soil with 0.65% total volatile solids) was measured for 4 days in three two‐liquid‐phase (TLP) slurry systems each containing 30% (w/v) soil but different volumes of silicone oil (2.5%, 7.5%, and 15% [v/v]). Except for chrysene, a high percentage of these PAHs was transferred from soil to silicone oil in the TLP slurry system containing 15% silicone oil. Rapid PAH transfer occurred during the first 8 h, probably resulting from the extraction of nonsolubilized and of poorly sorbed PAHs. This was followed by a period in which a slower but constant transfer occurred, suggesting extraction of more tightly bound PAHs. Second, a HMW PAH‐degrading consortium was enriched in a TLP slurry system with a microbial population isolated from a creosote‐contaminated soil. This consortium was then added to three other TLP slurry systems each containing 30% (w/v) sterilized soil that had been artificially contaminated with pyrene, chrysene, and benzo[a]pyrene, but different volumes of silicone oil (10%, 20%, and 30% [v/v]). The resulting TLP slurry bioreactors were much more efficient than the control slurry bioreactor containing the same contaminated soil but no oil phase. In the TLP slurry bioreactor containing 30% silicone oil, the rate of pyrene degradation was 19 mg L−1 day−1 and no pyrene was detected after 4 days. The degradation rates of chrysene and benzo[a]pyrene in the 30% TLP slurry bioreactor were, respectively, 3.5 and 0.94 mg L−1 day−1. Low degradation of pyrene and no significant degradation of chrysene and benzo[a]pyrene occurred in the slurry bioreactor. This is the first report in which a TLP system was combined with a slurry system to improve the biodegradation of PAHs in soil.
Applied Microbiology and Biotechnology | 1993
Yves Comeau; Charles W. Greer; Réjean Samson
The effect of inoculum preparation and density on the efficiency of remediation of 2,4-dichlorophenoxyacetic acid (2,4-D) by bioaugmentation was studied in non-sterile soil. A 2,4-D-degrading Pseudomonas cepacia strain (designated BRI6001) was used initially in liquid culture to determine the effects of pre-growth induction and of inoculum density. The time for complete 2,4-D degradation was reduced by 0.5 day for each log increase of inoculum density. In mixed (BRI6001 and soil bacteria) liquid cultures, a competition effect for 2,4-D became apparent at low inoculum levels (less than 10 105 cfu/ml BRI6001 for 108 cfu/ml soil bacteria) but only when the soil bacteria included indigenous 2,4-D degraders. In static non-sterile soil, the effect of inoculum density on 2,4-D degradation was comparable to that in liquid culture but only at high inoculation levels. At lower levels, a biological effect for 2,4-D degradation became apparent, as was observed in mixed liquid cultures, whereas at intermediate levels, a combination of biological, physical and chemical factors decreased the efficiency of bioaugmentation. The acclimation period for 2,4-D degradation in soil bioaugmented with BRI6001 reflected mainly the time required for cell induction and, presumably, for overcoming the physical limitation of diffusion of both 2,4-D and added bacteria in the soil matrix.
Water Research | 2010
Abdellah Ramdani; Peter Dold; Stéphane Déléris; Daniel Lamarre; Alain Gadbois; Yves Comeau
This study evaluated the potential biodegradability of the endogenous residue in activated sludge subjected to batch digestion under either non-aerated or alternating aerated and non-aerated conditions. Mixed liquor for the tests was generated in a 200 L pilot-scale aerobic membrane bioreactor (MBR) operated at a 5.2 days SRT. The MBR system was fed a soluble and completely biodegradable synthetic influent composed of sodium acetate as the sole carbon source. This influent, which contained no influent unbiodegradable organic or inorganic materials, allowed to generate sludge composed of essentially two fractions: a heterotrophic biomass X(H) and an endogenous residue X(E), the nitrifying biomass being negligible (less than 2%). The endogenous decay rate and the active biomass fraction of the MBR sludge were determined in 21-day aerobic digestion batch tests by monitoring the VSS and OUR responses. Fractions of X(H) and X(E): 68% and 32% were obtained, respectively, at a 5.2 days SRT. To assess the biodegradability of X(E), two batch digestion units operated at 35 degrees C were run for 90 days using thickened sludge from the MBR system. In the first unit, anaerobic conditions were maintained while in the second unit, alternating aerated and non-aerated conditions were applied. Data for both units showed apparent partial biodegradation of the endogenous residue. Modeling the batch tests indicated endogenous residue decay rates of 0.005 d(-1) and 0.012 d(-1) for the anaerobic unit and the alternating aerated and non-aerated conditions, respectively.
Water Research | 2013
Dominique Claveau-Mallet; Scott Wallace; Yves Comeau
The objective of this work was to evaluate the capacity of steel slag filters to treat a gypsum mining leachate containing 11-107 mg P/L ortho-phosphates, 9-37 mg/L fluoride, 0.24-0.83 mg/L manganese, 0.20-3.3 zinc and 1.7-8.2 mg/L aluminum. Column tests fed with reconstituted leachates were conducted for 145-222 days and sampled twice a week. Two types of electric arc furnace (EAF) slags and three filter sequences were tested. The voids hydraulic retention time (HRT(v)) of columns ranged between 4.3 and 19.2 h. Precipitates of contaminants present in columns were sampled and analyzed with X-ray diffraction at the end of tests. The best removal efficiencies over a period of 179 days were obtained with sequential filters that were composed of Fort Smith EAF slag operated at a total HRT(v) of 34 h which removed 99.9% of phosphorus, 85.3% of fluoride, 98.0% of manganese and 99.3% of zinc. Mean concentration at this systems effluent was 0.04 mg P/L ortho-phosphates, 4 mg/L fluoride, 0.02 mg/L manganese, 0.02 zinc and 0.5 mg/L aluminum. Thus, slag filters are promising passive and economical systems for the remediation of mining effluents. Phosphorus was removed by the formation of apatite (hydroxyapatite, Ca(5)(PO(4))(3)OH or fluoroapatite, Ca(5)(PO(4))(3)F) as confirmed by visual and X-ray diffraction analyses. The growth rate of apatite was favored by a high phosphorus concentration. Calcite crystals were present in columns and appeared to be competing for calcium and volume needed for apatite formation. The calcite crystal growth rate was higher than that of apatite crystals. Fluoride was removed by precipitation of fluoroapatite and its removal was favored by a high ratio of phosphorus to fluoride in the wastewater.