Abstract
In this work, the cross-flow microfiltration (CFMF) performance of a rough pale lager, produced in the industrial brewery Birra Peroni Srl (Rome, Italy), was assessed in a bench-top rig, equipped with a 0.8-μm ceramic hollow-fiber membrane module, to overcome the recognized inefficacy of back-flushing cleaning techniques in ceramic multi-channel monolithic modules. In total recycle CFMF trials, as the transmembrane pressure difference (TMP) was increased from 0.59 to 3.56 bar, the quasi-steady-state permeation flux (J*) tended to a limiting value increasing with the cross-flow velocity (v S). To minimize the overall membrane surface to be installed for a prefixed permeate recovery, it was found to be expedient to operate at the aforementioned high cross-flow velocity and TMP of 3.56 bar, thus obtaining quite a high quasi-steady-state permeation flux (mean, μ = 173 L m−2 h−1; standard deviation, sd = 7 L m−2 h−1; number of observations, N = 12). The energy consumption per liter of permeate collected was found to be practically independent of the operating variables v S and TMP selected (μ = 55 W h L−1; sd = 2 W h L−1; N = 21). Yet, a permeate flux greater than 100 L m−2 h−1 was achieved on condition that TMP was greater than 2 bar and v S varied from 4 to 6 m s−1. A few validation batch CFMF tests, carried out using pre-centrifuged, PVPP-stabilized, and cartridge-filtered rough pale lager at TMP = 3.56 bar, v S = 6 m s−1, and 10 °C under a predefined CO2 backwashing program, resulted in an average permeation flux (μ = 239 L m−2 h−1; sd = 24 L m−2 h−1; N = 2) by far greater than that (50–100 L m−2 h−1) claimed at 0–2 °C by the three CFMF processes commercially available. Finally, it was proved the easy transferability of the lager beer clarification and stabilization process, previously developed in a single-tube membrane module, to a ceramic hollow-fiber membrane module industrially upscalable.
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Introduction
The beer industry is potentially interested to replace conventional diatomaceous earth (DE) filters with cross-flow microfiltration (CFMF) systems to get rid of the environmental and safety concerns connected with filter-aid handling and spent filter sludge disposal. Unfortunately, the average beer permeation flux through polyethersulphone hollow-fiber membrane modules is about a fifth of that (250–500 L m−2 h−1) obtained with powder filters (Buttrick 2007; Fillaudeau et al. 2006).
In beer CFMF, the permeation flux is mainly controlled by the cake layer deposited onto the membrane surface (Cimini and Moresi 2014). Thus, several hydrodynamic techniques (i.e., co-current mode; pulsating flow; periodic stop of the transmembrane pressure difference; periodic back-flush or back-shock process; generation of Dean or Taylor vortices; gas–liquid or liquid–solid flow; use of turbulence promoters, such as baffle channel or stamped membrane) have been studied by Blanpain-Avet et al. (1999), Fillaudeau et al. (2007), Gan et al. (1997), Kuiper et al. (2002), and Sondhi and Bhave (2001) in order to enhance the CFMF performance.
To optimize the design of a back-flush regime, it is necessary to minimize permeate usage as back-flush medium so as to achieve pore clearance in the shortest time interval. Gan (2001) developed a multi-stage back-pulse routine capable of varying the CO2 feed pressure, the duration of the pulse, and the interval between the end of the pulse and opening of the permeate valve, as well as cycle frequency. These variables affected the membrane cleaning efficiency of the back-pulse and the overall permeate loss. By selecting appropriately such variables, Gan (2001) was successful at improving the 10-h average permeation flux to as much as 22 kg m−2 h−1, this value being the 400 % of that achieved during the cross-flow filtration formerly standardized (Gan et al. 1997).
In previous work (Cimini and Moresi 2014), laboratory-made green beers were pre-centrifuged to minimize the fouling contribution of yeast cells and aggregates and reduce their initial haze level to 1.0–1.3 EBC unit, and then clarified to a final haze ≤0.5 EBC unit in a bench-top plant, equipped with a ceramic single-tube membrane module having nominal pore size of 0.8 μm under constant feed superficial velocity (v S = 6 m s−1), transmembrane pressure difference (TMP = 3–4 bar), temperature (T = 10.0 ± 0.5 °C), and periodic CO2 back-flushing. In the circumstances, the average permeation flux ranged from 300 to 385 L m−2 h−1 thanks also to the efficacy of the CO2 back-flushing program applied to the single-tube membrane module. Such a procedure was further tested on a rough pale lager produced in the industrial brewery Birra Peroni Srl (Rome, Italy), thus obtaining an average permeation flux of 252 ± 21 L m−2 h−1 (Cimini and Moresi 2015). In addition, by stabilizing firstly pre-centrifuged beer with 0.5 g L−1 of regenerable polyvinylpolypyrrolidone (PVPP) at 0 °C for 24 h, removing the sediment, pre-filtering the stabilized beer via a 2.7-μm cartridge to get rid of residual PVPP particles, and finally cross-flow micro-filtering, it was possible not only to reduce the permeate chill haze to 0.31 ± 0.06 EBC unit but also to increase the average permeation flux to a value (337 ± 1 L m−2 h−1) quite near to that achievable with conventional DE-filters (Buttrick 2007).
The scaling-up of both operating conditions and back-flushing program from a ceramic single-tube membrane to a multi-channel monolithic module, such as for instance the Membralox® ceramic monolith type EP3740 (Pall Corporation 2007), is generally hampered by the difficulty of assuring appropriate and constant permeate flow rates throughout all the channels of the monolith. In fact, Doleček and Cakl (1998) showed that the contribution of some channels to the total permeation flux depended on either the ratio of skin layer to porous support permeability or the distance of a channel from the membrane outer surface. Thus, the cake layer deposited onto the membrane surface of the inner channels of the monolith may be poorly back-flushed by the local CO2 flow rate, thus yielding permeation fluxes quite lower than those obtained previously in a ceramic single-tube membrane.
The aim of this work was to assess whether the aforementioned combination of operating conditions and CO2 back-flushing program might succeed in clarifying pre-centrifuged rough pale lager using a novel ceramic hollow-fiber membrane module having the same nominal pore size of 0.8 μm while keeping both the permeate turbidity and average permeation flux practically unchanged.
Materials and Methods
Raw Materials
The rough pale lager used here was produced by the industrial Birra Peroni Srl brewery (Rome, Italy). It was withdrawn from the maturation tanks and stored at 0.0 ± 0.5 °C. Before CFMF testing, the rough lager samples were clarified using a laboratory centrifuge (Beckman mod. J2-21) at 6000×g and ≤4 °C for 10 min, and then diluted with de-ionized water as recommended by the brewmaster to reach an ethanol content near to the commercial one (4.7 ± 0.1 % v/v).
Equipment and Experimental Procedure
Beer clarification was carried out using the bench-top CFMF plant, previously described (Cimini and Moresi 2014). In this work, it was equipped with an α-Al2O3 hollow-fiber InoCep® membrane module type MM04 (Hyflux Ltd., Singapore; http://www.hyfluxmembranes.com/inocep-ceramic-hollow-fibre-membrane.html). Such a module consisted of 40 hollow fibers with an inside diameter (d HF) of 3 mm, an overall length (L HF) of 200 mm, and an effective membrane surface area (A m) of 0.04 m2, as well as a nominal pore size of 0.8 μm (type M800) and water permeability of 2500 L m−2 h−1 bar−1 at 25 °C. Figure 1a shows the overall (a) and front (b) views of the membrane module used.
Pre-centrifuged lager was fed to the membrane module using a centrifugal pump type HMS (Lowara, Montecchio Maggiore, Italy) with the following characteristics: maximum volumetric flow rate, 4200 L h−1; head, 40 m of water; and brake power, 0.45 kW.
Several hydraulic tests were carried out at 20 °C by varying TMP in the range of 0.5–4.0 bar, the main results of which being shown in Fig. 2. In particular, TMP was calculated as the average of the inlet and outlet pressures, minus permeate backpressure (Cheryan 1998):
where P in, P out, and P P are the experimental pressures at the inlet, outlet, and permeate ports of the membrane module used.
Despite the asynchronous motor driving, the centrifugal pump was piloted by means of a frequency inverter VF type Commander SK 0.75 k (Control Techniques, Powys, UK); the feed flow rate ranged from 400 to 2340 L h−1, this corresponding to a cross-flow velocity inside the membrane module (v S) varying from 0.4 to 2.3 m s−1. To apply the same operating cross-flow velocity (v S) of 6 m s−1, previously used to pilot a 0.8-μm ceramic single-tube membrane module with an inside diameter (d T) of 6 mm and a length of 0.5 m (Cimini and Moresi 2014), the novel hollow-fiber membrane module should have the same open cross-sectional area (a) of the tubular one, this involving the following condition
where n HF is the number of open hollow fibers needed. Thus, it was necessary to seal 36 out of 40 hollow fibers. This was carried out by applying a continuous bead of silicone adhesive (Silastic® E-RTV Silicone Rubber Kit, Dow Corning Co., Midland, MI, USA) over the inlet and outlet openings of such hollow fibers, the resulting silicone plug (Fig. 1c) remaining flexible even after curing and resisting chemicals including water. For reuse, a simple removal of the cured product was needed. To avoid any leakage during the operating conditions tested, all the silicone-sealed hollow fibers were covered by a stainless steel disk, as shown in Fig. 1d.
To assess the effects of TMP and v S on the volumetric permeate flux, pre-centrifuged rough lager samples were micro-filtered. The resulting retentate and permeate were continuously recombined and re-circulated through the membrane module under constant temperature (T = 10.0 ± 0.5 °C). Initially, TMP and v S were set at about 1 bar and 1.5 m s−1, respectively. As the quasi-steady-state permeation flux (J *) had been approached for as long as 15 min, TMP was step-wisely augmented from about 1 to 4 bar. Moreover, during any step, TMP was kept constant, while the cross-flow velocity was in sequence increased from 1.5 to 2.0, 2.5, 4.0, and 6.0 m s−1.
Two final batch validation tests were carried out using pre-centrifuged and PVPP-stabilized rough pale lager samples. In particular, the stabilization process was carried out as reported previously (Cimini et al. 2014; Cimini and Moresi 2015). More specifically, four 1.5-L cylindro-conical tanks were filled with pre-centrifuged rough lager. Then, an amount of 0.75 g of regenerable PVPP was added to start the stabilization process under a constant temperature (0.0 ± 0.5 °C). After 24-h incubation, the spent PVPP-polyphenol aggregates gone to the bottom of the tank were withdrawn. Finer residual aggregates were removed by vacuum filtration through 2.7-μm Whatman filters (cat. no. 1823 047). Final beer clarification was performed using the partitioned hollow-fiber membrane module by using two different procedures.
Firstly, two batch CFMF tests were carried out using the same operating conditions applied to a ceramic single-tube membrane module (TMP = 3.73 bar, v S = 6 m s−1, T = 10.0 ± 0.5 °C) in combination with the same CO2 backflush program (Cimini and Moresi 2015). As the permeation flux (J v) approached the quasi-steady-state flux (J*), the pressure in the retentate side was manually reduced to 1 bar and two electro-valves were automatically opened or closed using a programmable logic controller-based process (PLC) to adjust the pressure difference between the permeate and retentate sides at +3 bar for 2 min (Cimini and Moresi 2014). In this way, the CO2 back-flushing cycles differed one from another not only in duration but also in timing. The overall CFMF performance was determined by calculating the average permeation flux (J v,av) as follows:
where t max is the end time of the batch test. The function J v(t) was numerically integrated using the Simpson’s rule with a constant time increment of 1 min.
A second validation test was carried out in agreement with the operating procedure recommended by Hyflux Membrane Manufacturing (2010). More specifically, stabilized pale lager samples were submitted to batch CFMF under constant v S (1.5 m s−1) and T (10.0 ± 0.5 °C), while setting initially the feed input pressure (P in) and TMP at 2 and 0.96 bar, respectively. As soon as J v had declined to the quasi-steady-state flux (J*), TPM was step-wisely increased to 1.96, 2.92, and 3.84 bar by setting P in at 3, 4, and 5 bar, respectively. The overall performance of such a test was assessed by estimating J v,av using Eq. (3).
Membrane cleaning was performed as indicated by Gan et al. (1999). In details, the membrane module was initially rinsed with tap water. Then, it was filled with an aqueous solution of NaOH at 0.3 % (w/w) that was gradually heated up to 60 °C with a maximum heating rate of 4 °C min−1. Such a solution was then enriched with 0.5 % (v/v) hydrogen peroxide (at a percentage strength of 12 % v/v) and kept re-circulating through the membrane module at about 60 °C for not less than 15 min. Subsequently, the module was rinsed with fluent demineralized water at 60 °C for 15 min. Next, the demineralized water was laced with HCl till a content of 0.3 % (w/w) and kept re-circulating at about 60 °C for not less than 30 min. Final rinsing was performed using demineralized water, the temperature of which was progressively decreased from 60 to 20 °C. Such a cleaning procedure was generally sufficient to restore the initial hydraulic permeability of the membrane module; otherwise, it was repeated. Membrane cleaning was performed before any total recycle or validation test at time intervals ranging from 15 to 3.0–3.6 h, respectively.
Analytical Methods
The main characteristics (i.e., pH (EBC method no. 9.35); density, ρ (no. 9.43.1); viscosity, η (no. 9.38); turbidity or haze, H at 20 and/or 0 °C (no. 9.29); color, C (no. 9.6); and total phenol, TP (no. 9.11), β-glucan, BG (no. 8.11.1), real extract, RE, and original extract, OE (no. 9.4), and ethanol, A (no. 9.2.1), contents) of the beer or permeate samples were determined in compliance with the European Brewing Convention (2010) by referring to the EBC methods reported between round brackets.
Despite the pale lager used here was industrially produced, the variability in the rough pale lager samples submitted to CFMF testing was probably due to a few inevitable differences in wort production, lautering, fermentation, and beer maturation.
Statistical Analysis of Data
Hydraulic tests were triplicated and repeated at different times, while pale lager clarification tests using the hollow-fiber membrane module were duplicated to assess the error variance for the all the experimental campaign, as recommended by Montgomery (2005). Generally, the average coefficient of variation in the estimated permeation flux (J v) within data population was of the order of 10 %.
Finally, the main properties of centrifuged rough lager samples, as well as their corresponding permeates, were measured at least three times, and their means used for further analysis.
Results and Discussion
Hydraulic Tests for the Novel Ceramic Hollow-Fiber Membrane Module
The membrane module used here consisted of 40 hollow fibers with inside (d HF) and outside diameters of 3 and 4 mm and an overall length (L HF) of 200 mm. Such a bundle of ceramic tubes was hold together by a glue that irregularly covered the external surface of any tube. Thus, the manufacturer claimed that the nominal effective surface area of the membrane module was equal to 0.04 m2, this being quite smaller than the geometrical one (=π d HF L HF = 0.075 m2).
In the hydraulic tests, the experimental permeate mass flow rate (Q p) is a linear function of the transmembrane pressure difference (TMP) applied, being not affected by the feed superficial velocity for the lack of concentration polarization (Cheryan 1998), and can be expressed as follows:
with
where α is the specific water permeation rate, expressed in gram per second per bar, L W is the hydraulic permeability, commonly expressed in L m-2 s-1 bar-1, ρ W the density of water (in g L−1), and A m the effective membrane surface area (in m2).
Figure 2 shows Q p against TMP either for the membrane module as received (closed symbols) or after several subsequent hydraulic tests repeated over a time interval of 6 months (open symbols). In both cases, the analysis of variance for the linear model of Q p-vs.-TMP, including or not the intercept, allowed the intercept to be neglected, being statistically insignificant at the 95 % confidence level. Thus, Q P was proportional to TMP for v S varying from 0.5 to 1.5 m s−1.
Table 1 shows the specific water permeation rate (α W) together with the corresponding coefficient of determination (r 2) and number of observations (N), where α W was determined by using the least squares method. It can be noted a certain reduction in the membrane permeability as due to irreversible fouling. When the module was partitioned by sealing 36 out of 40 tubes to assure as high feed cross-flow velocities as 4–6 m s−1 in each hollow fiber using the centrifugal pump available, the hydraulic test allowed the specific water permeation rate for the partitioned module (α Wp) to be determined (Fig. 2). Thus, the effective membrane surface area of the partitioned module (A mp) was empirically estimated by assuming that all the hollow fibers of the membrane module had the same hydraulic permeability:
Such an effective membrane surface area was used to derive the volumetric permeation flux (J v) from the instantaneous permeate mass rate (Q p) as
where ρ P is the permeate density.
By referring to Table 1, during these CFMF trials, the experimental water permeability of the ceramic hollow fiber membrane module at 20 °C was equal to 1701 ± 54 L m−2 h−1 bar−1.
Effect of TMP and v S on Permeation Flux
Table 2 shows the main characteristics of the pale lager used in this work, as collected from the brewery maturation tank (RB) and as PVPP-stabilized and diluted with water as recommended by the Peroni brewmaster (F).
To verify the effects of TMP and v S on J v, the pre-centrifuged rough lager samples having turbidity of ∼1.16 EBC unit were micro-filtered, and the resulting retentate and permeate continuously recombined and re-circulated through the membrane module under constant temperature (10.0 ± 0.5 °C) by setting initially TMP and v S at about 1 bar and 1.5 m s−1, respectively. As the quasi-steady-state permeation flux (J *) had been approached for circa 15 min, the cross-flow velocity was sequentially raised from 1.5 to 6.0 m s−1. Such a procedure was then repeated by increasing TMP in sequence from about 1 to 4 bar, while resetting v S at 1.5 m s−1.
To mark better the shear effect of v S, the instantaneous permeation flux (J v) was used to estimate the corresponding overall membrane resistance (R T), as derived from Darcy’s law:
with
where η P is the permeate dynamic viscosity and R T, R m , R irr, and R rev are the overall membrane resistance, intrinsic membrane resistance, and resistances of the irreversible and reversible fouling layers, respectively. In particular, R rev includes concentration polarization and deposition of solids on the membrane surface (stationary cake layer), while R irr is due to interaction of the membrane with the particles and aggregates in the feed stream and comprises of the blocking of the pores entrance and internal fouling inside the pores.
As shown in Fig. 3, during any TMP step of the total recycle CFMF test, R T tended to increase with time (t) till reaching a quasi-steady-state value (R T *). As v S was increased under constant TMP, R T displayed a quick decrease and generally tended to a smaller R T * value. As TMP underwent a further step increase, v S was newly reduced to 1.5 m s−1. The aforementioned R T trend was generally reproduced in all the subsequent steps, the ratio between the corresponding quasi-steady-state overall membrane resistance (R T *) and intrinsic membrane one [R m = (1.62 ± 0.03) × 1011 m−1] being by far greater than unity. Moreover, the minimum R T * values resulted to be associated to v S = 6 m s−1. Thus, at TMP = 3.56 bar, the limiting flux (J *) resulted to be equal to 173 ± 7 L m−2 h−1 (Table 3).
Several studies have so far dealt with fluid dynamics in a porous tube under laminar (Vassilieff 1994; Munson-McGee 2002) and/or turbulent conditions (Mellis et al. 1993). In particular, the pressure drop along the porous tube length was found to be approximately parabolic in the laminar regime (Munson-McGee 2002). By referring to the main conclusions by Mellis et al. (1993), the pressure drop along a porous tube depends on axial flow rate and wall suction, such variables depending on the axial feed (Re F) and wall (Re W) Reynolds numbers, respectively:
where v W is the average wall velocity, this coinciding with the quasi-steady-state permeation flux (J*), expressed in m s-1.
According to Mellis et al. (1993), either at very low values of axial flow (Re F < 1000) and wall suction (Re W < 0.25) or for Re F > 20,000 and Re W ranging from 0 to 1.25, the axial pressure drop was found to be minimally affected by wall suction and practically coincided with that estimated via the Darcy equation for a solid wall tube (Toledo 2007):
where in this specific case, ΔP D is the pressure loss due to friction along the bundle of hollow fibers of given length L HF, and f the Fanning friction factor.
As shown in Table 3, the wall Reynolds number (Re W) ranged from 0.009 to 0.051, this ensuring the minimal effect of wall suction on the axial pressure drop both in the laminar and turbulent conditions (Mellis et al. 1993).
In this work, the Fanning friction factor (f) for laminar or turbulent flow in smooth circular pipes was estimated as follows (Toledo 2007):
The feasibility of calculating the Fanning friction factor using the smooth-tube model, even when the hollow fibers present a non-smooth surface in consequence of the progressive deposition of particles, was checked by referring to the measurements carried out by Pal et al. (2008) and Yazdanshenas et al. (2010). In particular, in the case of the ultrafiltration of simulated fruit juices consisting of pectin and sucrose using an organic polyphenylene ethersulfone membrane with a molecular mass cutoff of 30 kDa, the thickness of the cake thickness ranged from 10 to 16 μm, while J* varied from 9 to 33 L m−2 h−1 (Pal et al. 2008). A quasi-steady-state permeation flux (J*) of about 10 L m−2 h−1 was achieved during the cross-flow microfiltration of a rough non-alcoholic beer with quite a high haze at 20 °C (42.5 EBC unit) across a ceramic tubular membrane module with pore size of 0.45 μm, this being associated to the formation of a cake layer of 30–40 μm (Yazdanshenas et al. 2010). In the CFMF tests performed here, the rough beer was pre-centrifuged, PVPP-stabilized, and cartridge-filtered, this making the rough beer haze at 20 °C quite low (1.16 ± 0.02 EBC unit), as shown in Table 2.
By assuming J* as inversely proportional to the thickness of the cake layer, in this work, the fouling layer should have varied from 13 to 2 μm for v S increasing from 1.5 to 6 m s−1. In the circumstances, by assuming that the roughness (ε) of each hollow fiber is determined by the particles deposited, the relative roughness of the hollow fibers, that is, the ratio of their roughness to inner diameter (3 mm), would range from 6.7 × 10−4 to 4.3 × 10−3. By resorting to the Haaland equation (1983), that allows explicit calculation of the fiction factor (f) in quite good agreement with that estimated via the Colebrook equation (1938–39) when the Reynolds number and relative roughness are specified:
it was possible to assess that the relative errors of the solutions of Eqs. (15) and (13) or (14) for Re ranging from 3000 to 104 or 13,000 varied from −5 to +18 %, this making the Darcy friction factor estimated from Eq. (13) or (14) accurate enough owing to the large uncertainties in the Darcy friction factor in such flow regimes (Haaland 1983).
As shown in Table 3, the estimated pressure drop (ΔP D) was roughly the half of the experimental one (ΔP exp), this being estimated as the difference between the pressures analogically measured by the manometers located on the opposite ends of the membrane module. It is worth noting that ΔP D did not account for the so-called minor losses due to a few pipe fittings, such as the section enlargement to connect the 19.3-mm pipe to the 34-mm membrane housing, the section contraction to feed the hollow-fiber bundle, the section enlargement as the retentate flows out of the hollow-fiber bundle, and the final restriction encountered by the retentate flowing out of the membrane module. Among the methods generally used to account for the flow losses from friction in pipe fittings, contraction, or enlargement, those referring to the equivalent length (L e) or resistance coefficient (K) of any pipe fitting, that is, the length of pipe of the same size as the fitting or the number of velocity head terms (1/2 v S 2/g) that would give rise to the same pressure drop as the fitting, resulted in estimated minor losses (Anon 2012; Crane 1965) by far greater than those experimentally assessed by subtracting ΔP D from ΔP exp. Altogether, the largest contribution to the overall minor losses was due to the sudden contraction from the housing tube to the bundle of four 3-mm hollow fibers.
Figure 4 shows the combined effect of v S and TMP on the quasi-steady-state permeation flux J*. By operating at low v S values, such as 1.5–2 m s−1, J* tended to be independent of TMP at TMP values just greater than 0.6 bar. As v S was increased from 2.5 to 4 m s−1, the validity of the Darcy model extended up to TMP values of the order of 2 bar. Generally, the asymptotic J*-vs.-TMP relationship is attributed to the concentration polarization effect (Cheryan 1998). In fact, any increase in TMP results in a thicker or denser cake layer deposited over the membrane surface that increases the overall filter resistance and thus limits the permeation flux to the so-called limiting flux. Such a phenomenon, known as concentration polarization, is inherent to all cross-flow filtration processes for the membrane has different permeability for the various components of the solution or suspension (Cheryan 1998). The lower the cross-flow velocity, the lower the limiting flux becomes. From Fig. 4, it can be noted that at v S = 6 m s−1, J* was proportional to TMP for TMP < 4 bar. In fact, the analysis of variance for the linear model of J*-vs.-TMP, including or not the intercept, allowed the intercept to be neglected, being statistically insignificant at the 95 % confidence level. Thus, J* was predicted via the following least-squares regression equation:
where the lager permeability for the ceramic hollow-fiber membrane module was about the 3 % of the water permeability at 20 °C, previously assessed. The continuous line plotted in Fig. 4 illustrates the estimated J* values, while the broken lines refer to loci of the upper and lower confidence limits at the 95 % confidence level.
For all the operating conditions tested, Table 3 also lists the theoretical pump power (N P) needed to compress the rough lager feed (Q F) from the storage tank kept at atmospheric pressure (P atm) to the pressure (P in) registered by the gauge placed at the inlet port of the membrane module. Therefore, the total dynamic head (H P) of the centrifugal pump had to account for the differences in pressure, liquid elevation, and velocity between the source and destination, as well as for the pipe and pipe fitting friction losses and the pressure drop through the instrumentation and other items in the flow path of the liquid. In the bench-top plant used here, the static head difference between the rough beer tank and membrane module was regarded as negligible, the beer velocity head at the top level of the storage tank practically nil owing to the total recycle tests performed, while the pressure drop over the pipe fittings connecting the storage tank to the centrifugal pump and the latter to the membrane module was, by rule of thumb, assumed as one fifth of the experimental pressure drop across the membrane module itself. Thus, the theoretical power absorbed by the beer was evaluated as follows:
with
where Q F, Q P, and Q R are the feed, permeate, and retentate volumetric flow rates and a is the overall cross section of the membrane module, as defined by Eq. (2).
As shown in Fig. 5, whatever the cross-flow velocity and TMP applied, N P appeared to be proportional to J*:
In fact, the analysis of variance for the linear model of NP-vs.-J*, including or not the intercept, allowed the intercept to be neglected for the following reasons: (i) the intercept exhibited a negative value, statistically significant at the probability level of 0.024, but devoid of any physical meaning; (ii) the coefficient of determination of Eq. (22) was greater than that pertaining to the empirical model including the intercept (r 2 = 0.907). The continuous line in Fig. 5 shows the N P values estimated using Eq. (22), while the broken lines refer to loci of the upper and lower confidence limits at the 95 % confidence level.
Thus, despite a certain scattering of data, the energy consumption per unit liter of permeate recovered was practically constant (μ = 55 W h L−1; sd = 2 W h L−1; N = 21). Of course, such a figure did not include the power transferred from the electric motor to the shaft of the centrifugal pump and from the blades to the lager to be clarified, this depending on their corresponding efficiencies. Nevertheless, not all combinations of the operating variables v S and TMP allowed a permeate flux greater than 100 L m−2 h−1 to be assured. As shown in Fig. 4, such a CFMF performance might be achieved at TMP > 2 bar and v S of 4–6 m s−1.
Validation Testing
The effectiveness of the CFMF operating conditions yielding the higher value of the quasi-steady-state permeation flux (173 ± 7 L m−2 h−1), that is, TMP = 3.56 bar and v S = 6 m s−1 (Table 3), was further established using pre-centrifuged, PVPP-stabilized, and 2.7-μm pre-filtered rough pale lager together with the CO2 backwashing program previously set up (Cimini and Moresi 2014). The main characteristics of the rough pale lager sample (F) were listed in Table 2.
Contrary, to previous tests carried out on a pure malt beer containing as much as 140–250 mg L−1 of β-glucans (Cimini et al. 2014), in this work, no enzymatic depolymerization pretreatment was performed, the β-glucan content of the rough pale lager used being as small as 9 ± 2 mg L−1 (Table 2). Moreover, the 24-h PVPP-stabilization allowed the original total phenol content (152 ± 5 mg L−1) to be reduced to 89 ± 2 mg L−1.
Figure 6 shows the time course of the experimental permeation flux (J v: open symbols), when using the aforementioned CO2 backwashing program. In the circumstances, the min-max variation in the quasi-steady-state (J*) ranged from 152 to 200 L m−2 h−1 (μ = 175 L m−2 h−1; sd = 20 L m−2 h−1; N = 19). Thanks to the periodic CO2 back-flushing, the average permeation flux (J v,av) improved to 239 L m−2 h−1 (sd = 24 L m−2 h−1; N = 2), as calculated using Eq. (3). Moreover, the beer permeate collected during these trials exhibited an average haze at 20 and 0 °C of 0.21 ± 0.01 or 0.44 ± 0.06 EBC unit, respectively. Thus, the permeated beer fulfilled the European Brewery Convention specification (2010) for a clear, bright beer (<0.6 EBC unit).
Figure 6 also compares the typical time course of J v (closed symbols) for a similar pale lager sample previously submitted to batch CFMF through a 0.8-μm ceramic single-tube membrane module under practically the same operating conditions (i.e., TMP ≈ 3.73 bar, v S = 6 m s−1, T = 10.0 ± 0.5 °C, and periodic CO2 back-flushing), as extracted from Cimini and Moresi (2015). In that case, the mean values of J * and J v,av resulted to be equal to 138 ± 8 and 337 ± 1 L m−2 h−1, respectively (Cimini and Moresi 2015).
Despite the average permeation flux obtained was just the 71 % of that achieved with the single-tube module, the CFMF performance of the hollow-fiber membrane module tested here was on the whole by far greater than that (80–100 L m−2 h−1) claimed at 0–2 °C by the three CFMF processes commercially available (i.e., the Norit process filtering rough beer, previously sedimented under refrigeration, across 0.45-μm polyethersulfone hollow-fiber modules, and the Pall or Alfa Laval process filtering pre-centrifuged rough beer through 0.65-μm polyethersulfone hollow-fiber or flat-sheet membrane modules, respectively) (Buttrick 2007). Moreover, filtering rough beer at 0–2 °C was found to be useless provided that the CFMF unit had been fed with pre-centrifuged, PVPP-stabilized, and cartridge-filtered rough beer (Cimini and Moresi 2015).
Moreover, since the effectiveness of CO2 back-flushing previously assessed in a single-tube module (Cimini and Moresi 2014, 2015) is highly likely irreproducible in a multi-channel one (Doleček and Cakl 1998), the use of such a novel hollow-fiber membrane module appeared to be the only way to transfer the lager beer clarification and stabilization process previously developed (Cimini and Moresi 2015) from a bench-top rig to an industrial-scale plant.
To assess further the efficacy of the above operating procedure, another validation test was performed to simulate the procedure generally applied to counterbalance typical flux decay during the operation of industrial dead-end or cross-flow filters, this involving a progressive or a step by step increase in TMP while keeping the cross-flow velocity constant (Noordman et al. 2001; Hyflux Membrane Manufacturing 2010).
Figure 7 shows the time course of the experimental permeation flux (J v), as observed when setting v S at 1.5 m s−1 and fixing the initial TMP at 0.96 bar. As soon as the permeation flux had reached the quasi-steady-state permeation flux, the pressure (P in) at the input port of the membrane module was increased of about +1 bar. Such a procedure was continued till a final P in value of 5 bar. Despite a sudden increase in J v had been detected immediately after any step increase in the feed input pressure, J v tended to decline with time to J*. Altogether, the mean values, standard deviations, and numbers of observations of J* and J v,av resulted to be equal to (μ = 42 L m−2 h−1; sd = 8 L m−2 h−1; N = 35) and (μ = 64 L m−2 h−1; sd = 7 L m−2 h−1; N = 2).
It can be noted that the average permeation flux of the last validation test was fully in line with that claimed by Hyflux Membrane Manufacturing (2010) when setting v S = 2 m s−1 and increasing TMP step by step from 1.7 to 5.7 bar. Moreover, it was possible to confirm the indifference of J* to v S and TMP in the ranges of 1.5–2 m s−1 and 2–4 bar, respectively, as shown in Fig. 4.
By comparing the overall performances of the validation tests shown in Figs. 6 and 7, the procedure involving the operation at v S = 6 m s−1 and TMP = 3.56 bar resulted to be the most expedient for the following reasons: (i) the average permeation flux was about four times greater than that suggested by the hollow-fiber membrane module manufacture, this reducing the depreciation and maintenance costs of the CFMF unit; (ii) the theoretical electric energy consumed per liter of beer permeated collected was practically constant, as shown by Fig. 5.
Conclusions
The lager beer clarification and stabilization process previously developed using a 0.8-μm ceramic single-tube membrane module was successfully tested in the same bench-top rig equipped with a 0.8-μm ceramic four hollow-fiber membrane module to overcome the recognized inefficacy of back-flushing cleaning techniques in ceramic multi-channel monolithic modules.
In total recycle CFMF trials that were used to simulate pale lager clarification in the continuous mode, the quasi-steady-state permeation flux (J*) exhibited the typical phenomenon of concentration polarization with a limiting flux increasing with the cross-flow velocity (v S). Particularly, at v S = 6 m s−1 and TMP in the range of 0.59–3.56 bar, J* was proportional to TMP, yielding a pale lager permeability as small as the 3 % of the water permeability at 20 °C. By relating the theoretical pump power (N P) needed to feed appropriately the membrane module to the corresponding quasi-steady-state permeation flux, an average electric energy consumption of 55 ± 2 W h per unit liter of permeate collected was assessed, this value being practically independent of the operating variables v S and TMP selected. Yet, a permeate flux greater than 100 L m−2 h−1 was achieved provided that TMP was greater than 2 bar and v S varied from 4 to 6 m s−1.
A final validation batch CFMF test was carried out using pre-centrifuged, PVPP-stabilized, and cartridge-filtered rough pale lager by setting TMP to 3.56 bar and v S to 6 m s−1 under predefined CO2 backwashing program, thus obtaining an average permeation flux of 239 ± 24 L m−2 h−1 by far greater than that claimed by the three CFMF processes commercially available.
Finally, such operating procedure was found to be even more expedient than that suggested by the ceramic hollow-fiber membrane module manufacturer. In fact, the operation suggested by the membrane manufacture (i.e., v S = 2 m s−1 under a progressive increase in TMP from about 1.7 to 5.7 bar) resulted in an average permeation flux about four times smaller than that achieved with the alternative procedure examined in this work.
Nomenclature
- a:
-
Cross-sectional area of the hollow-fiber membrane module, as defined by Eq. (2) [m2]
- A:
-
Alcohol content of beer [%v/v]
- Am:
-
Effective membrane surface area [m2]
- BG:
-
β-Glucan content of beer [mg L−1]
- C:
-
Beer color [EBC unit]
- CFMF:
-
Cross-flow microfiltration
- dHF:
-
Inside diameter of each ceramic hollow fiber [m]
- dT:
-
Inside diameter of the tubular membrane module [m]
- DE:
-
Diatomaceous earth
- f:
-
Fanning friction factor [dimensionless]
- H:
-
Beer turbidity [EBC unit]
- HP:
-
Total dynamic head of the centrifugal pump [m]
- J*:
-
Quasi-steady-state permeation flux [L m−2 h−1]
- Jv:
-
Instantaneous volumetric permeation flux [L m−2 h−1]
- Jv,av:
-
Average volumetric permeation flux, as defined by Eq. (3) [L m−2 h−1]
- K:
-
Resistance coefficient of any pipe fitting [dimensionless]
- Le:
-
Equivalent length of any pipe fitting [m]
- LHF:
-
Length of each ceramic hollow fiber [m]
- LW:
-
Hydraulic permeability [L m−2 h−1 bar−1]
- nHF:
-
Number of open hollow fibers [dimensionless]
- N:
-
Number of observations [dimensionless]
- NP:
-
Theoretical pump power [W]
- OE:
-
Beer original extract [°Plato]
- Patm:
-
Atmospheric pressure [Pa]
- Pin:
-
Pressure at the inlet port of the membrane module [Pa]
- Pout:
-
Pressure at the outlet port of the membrane module [Pa]
- PP:
-
Pressure at the permeate port of the membrane module used
- PVPP:
-
Polyvinyl-polypyrrolidone
- QF:
-
Feed volumetric flow rate [m3 s−1]
- Qp:
-
Permeate mass flow rate [g s−1]
- QP:
-
Permeate volumetric flow rate [m3 s−1]
- QR:
-
Retentate volumetric flow rate [m3 s−1]
- r2:
-
Coefficient of determination
- RB:
-
Rough beer
- RE:
-
Beer real extract [°Plato]
- ReF:
-
Axial feed Reynolds number, as defined by Eq. (9) [dimensionless]
- ReW:
-
Wall Reynolds numbers, as defined by Eq. (10) [dimensionless]
- Rirr:
-
Irreversible fouling resistance [m−1]
- Rm:
-
Intrinsic membrane resistance [m−1]
- Rrev:
-
Reversible fouling resistance [m−1]
- RT:
-
Overall membrane resistance [m−1]
- RT*:
-
Quasi-steady-state overall membrane resistance [m−1]
- T:
-
Process temperature [°C]
- sd:
-
Standard deviation
- t:
-
Process time [s or h]
- tmax:
-
End time of any rough beer permeation test [h]
- TMP:
-
Transmembrane pressure difference [bar]
- TP:
-
Total phenolic content [mg L−1]
- vS:
-
Cross-flow velocity [m s−1]
- vW:
-
Average wall velocity [m s−1].
Greek Symbols
- αW:
-
Specific water permeation rate [g s−1 bar−1]
- ε:
-
Ηollow-fiber roughness (mm)
- ΔPD:
-
Pressure drop due to friction in smooth circular pipes [Pa]
- ΔPteo:
-
Theoretical pressure drop due to friction in smooth circular pipes [Pa]
- η:
-
Dynamic viscosity [mPa s]
- μ:
-
Mean value
- ρ:
-
Density [kgm−3]
Subscripts
- av:
-
Average
- exp:
-
Experimental
- F:
-
Referred to beer feed
- p:
-
Related to the partitioned hollow- fiber membrane module
- P:
-
Referred to permeate
- R:
-
Referred to retentate
- W:
-
Referred to water
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Acknowledgments
This research was supported by the Italian Ministry of Instruction, University and Research, special grant PRIN 2010-2011-prot. 2010ST3AMX_003.
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Cimini, A., Moresi, M. Pale Lager Clarification Using Novel Ceramic Hollow-Fiber Membranes and CO2 Backflush Program. Food Bioprocess Technol 8, 2212–2224 (2015). https://doi.org/10.1007/s11947-015-1575-z
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DOI: https://doi.org/10.1007/s11947-015-1575-z