HYDRODYNAMICS IN A TWO-COMPARTMENT BIOREACTOR

 

E.B. DE JESUS , L.R.P. DE ANDRADE LIMA, L.A. BERNARDEZ   and   P.F. ALMEIDA

Department of Materials Science and Technology, Federal University of Bahia, Rua Aristides Novis, 2, Salvador, Bahia, Brazil CEP 40210-630. E-mail: ebjesus@ufba.br, lelo@ufba.br

Industrial Engineering Graduate Program, Federal University of Bahia, Rua Aristides Novis, 2, Salvador, Bahia, Brazil CEP 40210-630. E-mail: leticiab@ufba.br, pfa@ufba.br

 

Cite this arcicle as:

E.B. DE JESUS, L.R.P. DE ANDRADE LIMA, L.A. BERNARDEZ   and   P.F. ALMEIDA (2017) “HYDRODYNAMICS IN A TWO-COMPARTMENT BIOREACTOR”, Latin American Applied Research, 47(1), pp 23-28.

 

Abstract-- Upflow two-compartment packing-free/packed-bed bioreactors have been used in petroleum microbiology due to their similarity with the oil field close to the injection or production wells. This two-compartment configuration gives a particular hydrodynamics to the liquid phase. In this study the hydrodynamics of a pilot reactor filled with glass beads was studied using tracer experiments. The residence time distribution was calculated and interpreted. The results for interstitial Reynolds number (ReLi <0.3) show curves with a peak at the beginning and a long tail that is distorted by the solution flow rate. A model composed of a continuous stirred tank, plug flow and cross-flow reactors was used to describe the flow patterns.

Keywords-- Hydrodynamic, Packed-bed reactor, Residence time distribution.

I. INTRODUCTION

Petroleum microbiology investigate bacteria isolation, identification, growth and inhibition focus on the oil recovery enhancement or depletion, in addition to the souring control, which is a major problem to the oil industry (Ollivier and Magot, 2005; Callbeck et al., 2011; Bernardez et al., 2012). The most used bioreactors for petroleum microbiology studies are upflow packed-bed reactors due to their large surface area for the attachment of microorganisms and reduced bioreaction time. However, to simulate the oil field close to the injection or production wells these reactors operate at low flow-rate and should have a large empty space at the entrance. This two-compartment configuration gives a particular hydrodynamic behavior to this bioreactor and simulates the oil wall injection region, where the sulfate reducing bacteria are most concentrated in an oil field (Ollivier and Magot, 2005).

Previous results of tracer experiments for upflow packed-bed reactors showed that their hydrodynamic behavior is close to the ideal plug-flow, but in most cases there is a significant axial dispersion and exchange with a stagnant zone. The liquid axial dispersion and holdup for packed-bed reactors can be correlated with the liquid flow rate using the superficial (ReLi=udprL/mL) or interstitial (ReLi=udprL/emL) Reynolds numbers, where u is the superficial velocity of the liquid phase (u=QL/S)), dp is the average size of the solid particles in the reactor bed, rL is the density of the liquid, mL is the viscosity, e is the bed porosity, QL is the liquid flow rate, and S is the cross section area of the porous bed (Backer and Baron, 1994; Bayraktar and Mehmetoglu, 2001; Méndez-Romero et al., 2011; Bernardez et al., 2008).

The hydrodynamics of an one-compartment upflow bioreactor was presented recently (Bernardez et al., 2008). The liquid flow rates used were 2.6, 14.5 and 34.5 mL/min, which corresponds to interstitial Reynolds numbers for the liquid phase of 0.096, 0.52 and 1.26. The results showed that at high flow rates the reactor behaves predominantly like a plug-flow reactor  which is distorted by the presence of small axial dispersion and an interaction with a stagnant zone, and at low flow rates both the dispersion and the interaction with a stagnant zone are significant. In addition, there is by-passing at low and intermediate flow rates. In this case the average residence time of the solution was close to the nominal residence time. A similar behavior was observed by Mendez-Romero et al. (2011) to evaluate a packed bed reactor filled with rock fragments.

Recently the hydrodynamics of a two-compartment bioreactor was addressed and phenomenological models for the two zones, that included an exchange between dynamic and stagnant regions, bypass and stirred-tank reactor was used to fit the residence time distribution curves (Iliuta et al., 2015). This bioreactor has some similarity with the reactor presented in this study; however, it is a two compartment packing-free/packed-bed bioreactor instead of a packed-bed/packing-free bioreactor.

The bioreactor presented in this study differs from the others because present a lower compartment empty of porous bed, which mimics the space due to the well in an oil field. This feature gives the bioreactor a standard feature of flow that must be considered, mainly because the region of interest of microbiological processes involving bacteria occurs in the vicinity of water injection wells.

The arrangement of ideal reactors (continuous stirred and plug flow) is the simplest approach to describe the hydrodynamics of non-ideal reactors. The reactor configuration and the parameters of the models can be estimated using a curve fit method based on a least-square criterion which is minimized with respect to the model parameters. This solution does not involve a strict phenomenological model or differential equation, but it gives insights into the phenomenology which can help the further elaboration of phenomenological models. The details of the residence time distribution (RTD) calculations used in this work were previously described (de Andrade Lima and Hodouin, 2005).

 

Figure 1. Schematic representation of the experimental setup used in the column residence time distribution studies. The numbers stand for: 1) distilled water reservoir, 2) constant flow high pressure pump, 3) tracer reservoir, 4) constant flow high pressure pump, 5) the reactor bottom empty compartment, 6) the reactor porous bed, 7) small tank with a hole in the bottom and pH electrode, 8) waste solution reservoir, 9) pH meter, and 10) computer.

The main objective of this study is to describe the hydrodynamic behavior of a pilot-scale upflow packed-bed bioreactor that has two compartments (a porous bed and a bottom reservoir) and operates at low Reynolds numbers (ReLi<0.3).

II. MATERIALS AND METHODS

Figure 1 shows the schematics of the experimental setup used in the present study. It consists of an 8.8 cm internal diameter, 64.0 cm high  packed column that is  a  super-duplex stainless steel cylindrical bioreactor that has four lateral sampling ports, closed with high pressure vanes. The distance between the sampling ports is 14.0 cm. The upper zone of the reactor, which consists of an 8.8 cm internal diameter, 58.0 cm high, was filled with 3.0 mm glass beads, which gives a bed porosity of 40 %. The bottom of the reactor has an empty space measuring 7.5 cm in internal diameter, and 6.0 cm high. Separating these compartments there is a one millimeter thick plate with holes of one millimeter of diameter that supports the packed-bed. Distilled water was introduced at the bottom of the column by a dual piston constant flow HPLC pump and a PTFE-tubing (polytetrafluorethylene), and collected at the top of the column.

The injection of distilled water and the tracer (sulfuric acid) was done with two independent HPLC pumps (see Fig. 1). The liquid solution was collected in a small reservoir with a small hole in the bottom, which retained a small volume of the solution and enabled the measurement of pH using the Marconi pHmeter, model PA 200. The pH measured as a function of time was read by a personal computer and ASCII (American Standard Code for Information Interchange) files were used to perform the subsequent analysis. The measured pH was used to evaluate the tracer concentrations. Before starting the experiments, distilled water was injected into the reactor to saturate the bed. After each experiment, the bed was continuously rinsed with distilled water to assure that the tracer was removed and to assure steady state condition in the flow rate. All experiments were conducted at room temperature and atmospheric pressure. The hydrodynamic behavior of the reactor was studied for the liquid flow rates equal to 2.6, 3.5, 5.0, 7.5, 10.0, and 12.0 mL/min. The interstitial Reynolds numbers for the liquid phase are: 0.05, 0.08, 0.11, 0.16, 0.22, and 0.26 respectively.

The calculations related to the treatment of the acquired pH data and the calculation of the residence time distributions were done using in-house code developed using MATLAB v.7 (from MathWorks Inc).

III. RESULTS AND DISCUSSIONS

The hydrogen ion concentration in the solution as a function of time was calculated from the pH values ([H+] = 10-pH). The residence time distribution E(t) and the average residence time () were calculated as described in previous studies (de Andrade Lima and Hodouin, 2005; Bernardez et al., 2008).

Figure 2 shows the results of input-output response tests and relates the variation of the H+ ion concentration with time for the flow rates equal to 2.5, 5.0 and 12.0 mL/min. The reproducibility of the distributions was assessed with the repetition of five of the six operating conditions tested. The plots show that the distributions are reproduced in the initial region of the curve and that there is variable behavior at the end of the curves. The presence of an initial peak followed by an exponential decay function is a characteristic behavior of packed-bed reactors. At low flow rates the reactor exhibits a similar hydrodynamic pattern to plug-flow reactors distorted by the presence of strong axial dispersion and the presence of stagnant zones. At intermediate flow rates the axial dispersion and stagnation zones are reduced. At high flow rates the axial dispersion and stagnation zones are small and the presence of preferential flow channels is noted. In all cases, the delay in the output of the tracer may be related to the reactor water inlet and outlet systems which are composed of pipes, valves and a small reservoir for the pH electrode. Since the zones of stagnation and preferential flow paths may be related to the existence of a void at the bottom of the reactor, this may result in the retention of some of the tracer, releasing it slowly over time. This characteristic may explain the hydrodynamic behavior of the difference between the rated reactor and those studied by Bernardez et al. (2008) and Méndez-Romero et al. (2011).

The nominal residence time of the solution in the reactor can be calculated from the actual volume of the reactor and the solution flow rate. In the present case the volume of the reactor is given by the volume of the porous bed plus the volume of the empty compartment located at the bottom. The total reactor volume in liters is:

                                      (1)

where the db is the diameter of the reactor bed, hb is the length of the reactor bed, dr is the diameter of the reactor empty compartment, hr is the length of the reactor empty compartment, and e is the bed porosity. It can be seen that the empty compartment located at the bottom of the reactor houses 15.8% of the actual volume of the reactor. The nominal residence time in hours is given by:

, (2)

where the QL is the solution flow rate in mL/min.

(a)

 

(b)

 

(c)

 

Figure 2. Reactor impulse response for different flow rates (mL/min): a) 2.5, b) 5.0, c) 12.0.

(a)

 

(b)

 

Figure 3. a) Average and nominal solution residence time as a function of the solution flow rate. b) The deviation from the plug-flow behavior of the solution residence time as a function of the solution flow rate.

      Figure 3a shows the nominal and the measured average residence times for the reactor as a function of the flow rates. The correlation between the average residence time and flow rate is given by:

,               (3)

It is interesting to note that and tn decrease with the flow rate enhancement; however, the average residence time curve is higher than the actual nominal residence time which indicates the presence of stagnant and mixing zones. These results are different from those seen by Bernardez et al. (2008) and Mendez-Romero et al. (2011) who observed similarity between and tn. Figure 3b shows the evolution of the difference between the average and nominal residence time with the flow rate. It is evident that the flow rate enhancement reduces the mixing and the exchange with the stagnant zones and the hydrodynamics become closer to plug flow behavior.

Figure 4 shows the relationship between the ratio of the nominal residence time and the average residence time (Q = tn/t) as a function of the interstitial Reynolds number. The plot shows that as the Reynolds number increases, the Q also increases, which causes a reduction in the average residence time associated with the reduction in the stagnation zones. The correlation between the ratio of the nominal residence time and the average residence time as a function of the interstitial Reynolds number in the present case is given by:

,        (4)

To model the reactor, an arrangement of simple ideal reactors was used. A large number of combinations were evaluated to represent the different hydrodynamic behavior of the reactor and the results shown here are those with the best fit with a limited number of parameters. Figure 5 presents a generic scheme of the arrangement of CSTRs and CSTRs with exchange with a stagnant zone, which describes the hydrodynamic behavior of the upflow packed-bed reactor. In this superstructure K, L, M, and N stand for the number of reactors in the cascade of each branch and α and β stand for the fractions of flow rate directed to each branch of the arrangement.

Figures 6a, 6b and 6c show the experimental and the calculated data fitted with the superstructure (Fig. 5), for 2.5, 7.5, and 12.0 mL/min. The main features of the curves are well represented by the generic hydrodynamic model (Fig. 5).

Figures 7a to 7e summarize the relationship between the volumes of the elements of the model that compose the reactor for different flow rates. At low flow rate (Figs. 7a and 7b) the model is described by a PFR in series with a CSTR with active and dead zones and a cascade of CSTRs.

In both cases (Figs. 7a and 7b), most of the hydrodynamic behavior of the reactor is explained by the active zone of the CSTR followed by the exchange with the stagnant zone, probably related with the reactor res ervoir at the bottom and the interaction with the stagnant liquid found around the glass beads. The PFR component is explained by the pipes and the reactor entrance and exit. The CSTR cascade, which increases with the flow rate, seems to be related to the solid bed axial dispersion.



Figure 4. The ratio nominal to average solution residence time (Q = tm/t) as a function of the interstitial Reynolds number.

Figure 5. Generic process flow diagram to the two-compartment packing-free/packed-bed.

(a)

 

(b)

 

(c)

 

Figure 6. Experimental and fitted (dash line) residence time distribution as a function of the solution flow rate (in mL/min): a) 2.5, b) 7.5, and c) 12.

 

At intermediate flow rate (Figs. 7c and 7d) the hydrodynamic model is described by a PFR in series with two parallel branches. In the main branch there is a CSTR with active and dead zones in series with a cascade of CSTRs. In the secondary branch, there is a cascade of CSTRs that account for a small fraction of the reactor volume. The main components are analogous to the previous case, but the secondary branch is a bypass caused by the direct flow of the liquid without interact tion with the stagnant liquid found at the bottom reservoir or associated with the glass beads.



Figure 7. Hydrodynamic models for the two-compartment packing-free/packed-bed reactor as a function of the solution flow rate (in mL/min): a) 2.5, b) 5, c) 7.5, d) 10, and e) 12.

 

At high flow rate (Fig. 7e) the hydrodynamic model is described by a PFR in series with three parallel branches. In the main branch there is a CSTR with active and dead zones in series with a cascade of CSTRs. In the secondary branches, there are cascades of CSTRs that account for most of the reactor volume. The main components are analogous to the previous case, but the secondary branches are bypasses of liquid flow with axial dispersion through the solid bed.

The results are consistent with those presented by Iliuta et al. (2015) who used a CSTR with active and dead zones for modeling of the residence time distribution of the liquid phase in the packing-free region in a two-compartment packed-bed/packing-free bioreactor.

IV. CONCLUSIONS

The residence time distribution of the liquid phase in an upflow two-compartment packing-free/packed-bed reactor was evaluated using tracer experiments. A schematic model of a continuous stirred tank, plug flow and cross-flow reactors was used to describe the flow patterns. The results for flow rates ranging from 2.5 to 12.0 mL/min show non-ideal behavior with variable axial dispersion, bypassing and stagnant zones.  The axial dispersion is reduced with increasing flow rate. For low flow rates (2.5 and 5.0 mL/min) no bypassing was detected and the presence of strong axial dispersion and a small interaction with a stagnant zone occurred. For intermediate flow rates (7.5 and 10.0 mL/min) bypassing occurs and both the axial dispersion and the interaction with a stagnant zone are strong. For high flow rates (12.0 mL/min), the presence of bypassing is enhanced while the axial dispersion and the interaction with a stagnant zone are small.

ACKNOWLEDGEMENTS

This research was supported by the CNPq (Brazil) (Projects No. 475810/2008-2, 476344/2009-5, 550537/2009-0, 309707/2010-2, 480181/2011-0, and 402822/2013-7), Programa Nacional de Pós-Doutorado from CAPES (Brazil) and PETROBRAS (contract No. 00500022719.06.4).

REFERENCES

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Méndez-Romero, D.C., A. López-López, R. Vallejo-Rodríguez and E. León-Becerril, “Hydrodynamic and kinetic assessment of an anaerobic fixed-bed reactor for slaughterhouse wastewater treatment,” Chem. Eng. Process., 50, 273-280 (2011).

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Received: August 19, 2015.

Sent to Subject Editor: December 17, 2015.

Accepted: September 5, 2016.

Recommended by Subject Editor: Mariano Martin Martin