METHOD AND APPARATUS FOR THE UTILIZATION OF ZERO FIBER AND OTHER SIDE STREAMS
20230357816 · 2023-11-09
Inventors
Cpc classification
C12M23/58
CHEMISTRY; METALLURGY
C12M21/18
CHEMISTRY; METALLURGY
C12P7/40
CHEMISTRY; METALLURGY
Y02E50/30
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
Y02P20/10
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
C12P39/00
CHEMISTRY; METALLURGY
International classification
C12P39/00
CHEMISTRY; METALLURGY
C12M1/40
CHEMISTRY; METALLURGY
C05F17/20
CHEMISTRY; METALLURGY
Abstract
In the combined process for several biorefinery products obtained from a UMC (Undefined Mixed Culture) type of reaction it is possible to obtain biochemicals, energy gases, soil improvement etc. from a MPBU (Multipurpose Biorefinery Unit). The economically beneficial as well as environmentally sustainable results of the arrangement are demonstrated by the integrated process using two reactor systems with zero fiber for the production of lactate (in both the reactors pools 1 and 2). Additionally, mannitol can be produced in one of the reactor pools (number 2). It is possible to a. combine the processes taking into account their biochemical characteristics, b. produce gaseous substances for energy and industrial use, c. obtain organic fertilizers which can be microbiologically upgraded d. improve the adjustability for optimization of the various partial reactivities.
The chemical production occurs in two pools which advantageously are inoculated simultaneously.
Claims
1. Method for optimizing the simultaneous or interlinked production of (1) organic acids, such as lactate and (2) mannitol characterized in, that two reactor pools are used, which are the pool number 1 for the production of lactate or other SCFA's (Small Chain Fatty Acids), and the pool number 2 for the production of mannitol using rumen bacteria as biocatalysts in such a way that after the recovery of mannitol or even without it, the residual process fluid is advantageously applied to the pool number 1 for further elevating both the lactate and mannitol levels of the biorefining as a whole (
2. Method according to the claim 1 characterized in, that the inoculation of the two reactor pools is carried out simultaneously.
3. Method according to the claim 1 characterized in, that zero fiber or other cellulosic material in the reactor 1 is used as the main source of glucose in the reactor pool.
4. Method according to the claim 3 characterized in, that cellulolytic enzymes are used for the hydrolysis of the cellulose, preferably at least partially in the CBP mode, simultaneously with the microbial processes.
5. Method according to the claim 1 characterized in, that fructose containing side streams were used as the raw material source for mannitol production.
6. Method according to the claim 1 characterized in, that the mannitol is recovered either from the pool 2 into which the fructose and rumen bacteria had been added, or from the pool 1 if the residues of the pool 2 are transferred to pool 1 without prior recovery of the mannitol.
7. Method according to any of the claims 1-6 characterized in, that some kind of cellulosic material such as the zero fiber, was used in both of the pools number 1 and 2 amongst the other raw materials.
8. Method according to the claim 1 characterized in, that the purification of lactate or other organic acids can be carried out of the residues of both pools either separately or as combined to each other.
9. Method according to the claim 1 characterized in, that hydrogen in the bubble flow (
10. Method according to the claim 1 characterized in, that the final fraction with solid particles or suspension is collected for soil improvement or organic fertilization purposes.
11. Method according to the claim 10 characterized in, that the residual fraction of the biorefinery is upgraded as soil improvement by using bacteria of the species Clostridium pasteurianum or any other autonomously nitrogen-fixing species for increasing the soil nitrogen content available for the plant growth.
12. Method according to the claim 10 characterized in, that the final fraction is used for replacing or increasing the soil humic fraction,
13. Apparatus for using the method as described in the claim 1 characterized in, that the two pools are advantageously arranged conveniently into such a position with respect to each other that the residues of the pool 2 can be added the shortest way into the pool 1 in the process phase that corresponds to the time point in the latter pool and process (X point in
14. Apparatus according to the claim 13 characterized in, that the process fluid or flow or broth or suspension is moving forwards from the beginning to the end of the process by the help of rotors, screws, blows, paddlewheels or equivalent.
15. Apparatus according to the claim 13 characterized in, that sensors or other measurement systems for temperature, pH, turbidity, contents of various gases, conductivity, pO.sub.2, pCO.sub.2, impedance, viscosity, glucose or fructose content, or any other relevant or measurable parameter for the bioprocess can be situated at any point of the process or process flow in any of the pools.
16. Apparatus according to the claim 13 characterized in, that the process can be adjusted in any of the pools with respect to the chosen parameters at any time point during the process flow; for example at the temperature of 28-32° C. for the lactate-producing LAB population in the pool 1, and at 37-42° C. for the corresponding population in the pool 2.
17. Apparatus according to the claim 13 characterized in, that the process control and adjustment or addition of reagents or water is being facilitated by the results of the measurements.
18. Apparatus according to the claim 13 characterized in, that the mannitol is recovered by crystallization or by any other method carried out in a separate container or series of containers from the fluid of the pool 2.
19. Apparatus according to the claim 13 characterized in, that the lactate is the main product in pool 1, whereas it is the additional product in pool 2, but the same equipment can be used for its recovery in both cases.
Description
DESCRIPTION OF THE INVENTION
[0034] In biotechnical processes using biocatalysts, it is essential to implement the simultaneous planning strategies both for the growth and maintenance of the biocatalysts and for their reactions, as well as for the hardware design and adjustments of the bioreactors. The essential feature of this invention is to synchronize the biochemical and microbiological process with the design of the bioprocessing plant. These ideas have been tested in several pilot experiments, where both enzymes and microbial mixed cultures have been used in the pool-shaped reactors.
[0035] The pool construct allows the bioprocess fluid or broth or suspension to be moved forward while it is processed or adjusted. It is also easier to carry out the measurements of the process parameters alongside the progress within the reactors, or during the succession of the biochemical or microbiological reaction sequences. In the present invention, the pool shaped reactor system is illustrated in
[0036] This flexibility of the process control is important, not only for the timely recovery of chemical products but also for the collection of gaseous substances. For example, the hydrogen gas can be formed during a specific phase of the process. If the oxygen content of the fermentation broth is low enough, this leads to the formation of butyrate and hydrogen (
[0037] If the organic acids, such as lactate and propionate, are produced microbiologically from the slaughterhouse waste or from the potato industry waste, some members of the normal flora or the additional industrial strains of Clostridium pasteurianum could facilitate the formation of valeric acid (Den Boer et al. 2016; Schwede et al. 2017). The formation takes place as a consequence of the condensation reaction between lactate and propionate. Besides, the Clostridium pasteurianum strains or its closest relatives are strictly anaerobic bacteria which also produce hydrogen gas (H.sub.2), and bind atmospheric nitrogen (N.sub.2) in an autonomous fashion (Hakalehto 2016b). In fact, it has been proven out that the lactic acid bacteria can boost the onset of clostridial growth by their CO.sub.2 production (Hakalehto and Hänninen 2012; Hakalehto 2015a). This could make it possible to combine the production of H.sub.2 (for hytane gas mixture, for example) with the conversion of organic wastes into useful chemicals, such as organic acids (lactate, propionate, butyrate, acetate, valerate etc.). or 2,3-butanediol, butanol or ethanol, as well as with the production of sugar alcohols, such as mannitol, xylitol or sorbitol. This could lead to a biorefinery process, which could in the same or parallel units facilitate the production of [0038] 1. energy gases, [0039] 2. valuable chemicals, and [0040] 3. organic fertilizers or soil improvement agents,
in the process unit with one or several industrial strains which could function together with the natural microflora derived from the side stream in question. The above-mentioned microbiological method to upgrade the residual fraction by autonomous Nitrogen-fixing bacteria could remarkably improve the economics of the zero fiber processing, or alternatively that of any other biomass processing multi-strain or CBP-type of bioprocess. This could produce huge savings in: [0041] A. investment costs, as the production unit volumes go down, [0042] B. energy efficiency, as the power source is within the process, [0043] C. adjustments and control, which can be handled on the ecosystem level at best, [0044] D. removing at least a part of the gate fees in the treatment of the residual fraction and by bringing an important economical value for it
in the said manufacturing unit. The corresponding and required technologies could make it possible to learn to adjust the process for the numerous goods (gases, chemical commodities, fertilizers) according to the economic conditions and the demand in the market. Consequently, it is possible to build up a multipurpose biorefinery unit (MBPU) with low investment costs. It can obtain energy gases (hydrogen, methane, hytane) or electricity from the process itself. Such MBPU process, however, may also need clever partitioning of the process or unit operations.
[0045] Different organic materials and side streams can be produced in the MBPU. Besides the residual fractions of the forest, potato or slaughterhouse industries, also different agricultural or forestry wastes, as well as side streams of the sugar or brewing or fruit processing industries could be considered as potential raw materials. Since most of these raw materials consist of organic polymers, their hydrolysis is required. This could be carried out by acid or base, or by hot steam or water, or by some other physicochemical methods, as well as by enzymatic hydrolysis. In the latter kind of process, temperature changes could be utilized for improving the yield from the hydrolysis. The raw materials for the unit could include many other biomass sources besides the zero fiber, such as agricultural wastes, fruit waste, food industry wastes, sugar industry waste etc.
[0046] In addition to the two SCFA's (Small Chain Fatty Acids), lactate and propionate, it is possible to produce a third one, namely butyric acid (butyrate). This has been formed in the process utilizing the zero fiber and paunch as raw materials. It has been proven in our earlier studies that the CO.sub.2 emitted by lactic acid bacteria provokes and speeds up the growth of butyric acid clostridia (Hakalehto and Hänninen 2012, Hakalehto 2015a).
[0047] Typically for the production of the SCFA's their formation is peaking in the anoxic conditions. If the pH is around 6.5, the main product of the mixed fermentation is often propionate, at the pH of 5.5 it is butyrate, and at the pH of 4.5 acetate. Lactate is converted into other SCFA's (Hakalehto 2015b). The production of propionate, for example, can also get performed by a food-grade micro-organism Propionibacterium acidipropionici, which is accepted for food production by EFSA (European Food Safety Association).
[0048] In order to carry out the CBP type of reaction, one has to support it or at least is obliged to suppose that the conditions for the enzymatic hydrolysis will remain allowable during the accompanying microbial process. In turn, the continuous hydrolysis keeps the conditions ideal for microbial metabolism as it limits such regulatory functions as feedback inhibition for itself. Therefore, it is beneficial for the outcome, productivity and yield of the process to ensure the incessant enzymatic function in the production broth, as well as the boosting up of the desired microbiological reaction in a mixed metabolism situation. In fact, the CBP process is often easier to be converted into a continuous process. However, if the products are mixed or variable ones, the processing plan may include several reactor, tanks or pools for various partial processes or phases.
[0049] In practise, the challenges of the CBP often relate to the diffusion reactions, which means in practise that gradients or different zones are easily formed into the process. This is more likely in the big units. On the other hand, these gradients could also be advantageous for the process outcome, productivity and yield, provided that the gradients can be controlled well enough.
[0050] Therefore, with the intention of [0051] A. arranging suitable conditions throughout the reactor broth for both enzymatic hydrolysis and the microbial process, and [0052] B. controlling the gradients related to various reactions the equipment and method according to the present invention offers means to exercise such activities when pursuing the multi-strain or CBP-type of reaction in a biorefinery or equivalent.
[0053] In a big production unit a pool-type of reactor if often advisable for the improved options of control and sequential process mode. According to the present invention, it is possible to monitor and measure such parameters as temperature, pH, turbidity, concentrations of various gases, conductivity, pO2, pCO2, impedance, viscosity, glucose or fructose content or any other parameter. These measurements can be taken from the process broth moving on by the rotors, propellers, liquid blows, screws, paddlewheels or equivalent. The measurement can be taken from any point of the process, and the result can be used for the adjustments or for planning of the additions. It is also possible to move the process fluid from one point to another by pumping systems.
[0054] We have carried out the processing of slaughterhouse wastes (paunch and other fractions) together with molasses (US Patent Application (US20160251684A1) (Hakalehto 2016c)). In these cases the fructose of the molasses is converted into mannitol. When the molasses are added to the residual “zero fiber” fraction of the pulp and paper industries, this leads to the formation of organic acids, particularly lactic acid (Beckinghausen et al. 2019). Moreover, if paunch and molasses are added to this side stream, this also leads to the accumulation of mannitol in the favourable conditions in the multi-strain process.
[0055] In an advantageous mode of processing various wastes into mannitol and lactate, or into other organic acids, a mixed microbial culture of rumen bacteria can be used as the biocatalyst. This approach can be performed according to the procedure of the US Patent Application (US20160251684A1) (Hakalehto 2016c) These processes can be carried out simultaneously, namely the lactate and mannitol production, in the one and same reactor system. However, according to the present invention, the optimal process mode is a partially separated system of two pools (
[0056] One important aspect is the difference in the composition of the LAB microflora. The flora in the lactate production phase (out of the hydrolyzed cellulose) have the optimal temperature of 28-32° C., whereas the mannitol production is carried out by strains selected at 35-40° C. The former process takes about 90-100 hours to reach maximal production rate, and the latter one about 50-70 hours for the same level.
[0057] However, in the large-scale treatment of e.g. cellulosic waste combined with molasses, it turned out that the lactate process (
[0060] It is also noteworthy, that in lowered oxygen content, more butyric acid and hydrogen can be formed.
[0061] This synergism of two separated reaction is optimal and effective only when the processes are synchronized with the main processes starting in separate reactors or tanks or pools but to be combined in a delicate way as illustrated here (
[0062] After the mannitol production has reached its maximum, and the product recovered, for example by a separate reactor for crystallization, or by a series of reactors, the remaining active biological fluid can be added to the lactate production unit and into the lactate fermentation broth. There it can boost the lactate production. —During the mannitol production, the initial lactic acid bacteria (LAB) originating from the rumen contribute to the preservation of mannitol by keeping the pH low (Hakalehto 2016c). The division and initiation of the two processes in two reactors increase the production of both of the processes, as they can be adjusted and optimized separately for the beginning. However, it is advantageous to combine the residual fraction of the mannitol process into the ongoing lactate production, which brings also other synergistic benefits that can be achieved by this combination. Moreover, lactate is one of the main natural product of the rumen LAB, which, besides the stabilization of mannitol, also can be collected as a by-product from that process (pool number 2).
[0063] In order to boost mannitol production, the addition of fructose-containing substances into the containers served the purpose (
[0064] The production of such biochemicals serves as the core function in the conversion of biomass side streams into useful chemicals, energy gasses and organic fertilizers (
Example 1
[0065] In the industrial piloting of lactate production from the zero fiber, 600 litres of the cellulolytic material was treated with 1000 g of Viscamyl Flow and 750 g of Optidex enzymes. The hydrolysis phase prior to the microbial process lasted for 25 hours. For the hydrolysis 300 litres of water was added, 50% of which was obtained from the residual fraction of the previous runs. For the microbial inoculum, 51 kg of rumen biomass and 7 kg of sour milk were added 20 hours after the onset of the fermentation phase. Also 175 kg of molasses were added, together with the microbes and 65 litres of NaOH (40%) and 17 kg of CaCO.sub.3 for the pH adjustment during the process, as well as 21.5 kg of meat bone meal. The volume of the process water was increased by 127 litres during the process run. The pH was kept between 5.1-6.5 by the addition of NaOH, and the temperature was 30° C., which favoured the lactic acid bacteria derived from the lake. The steadily increasing lactate production is presented in
Example 2
[0066] In the simultaneous production of mannitol and lactate in the laboratory, the focus was in the optimization of the former substance, since the optimization of the lactate as a product was carried out as described in the Example 1. The mannitol production was boosted for the last quarter of the process run by adding some fructose syrup to the broth. The temperature for the hydrolysis was 40° C., and it was 37° C. for the mannitol fermentation. Ten litre buckets were used as containers or reaction vessels.
[0067] The hydrolysis phase took 12 hours, and the enzymes “Viscamyl Flow” (2 g) and “Optidex” (1.4 g) were added to the suspension of 1.5 litres of zero fiber (or some corresponding cellulolytic substrate) with 0.5 litres of water. For the following microbial inoculation, 3.5 litres of rumen contents or paunch were added to the container together with 2.1 kg molasses, 500 g of meat bone meal and 100 g of liver. The pH adjustment during the process was carried out with 70 ml NaOH (40%) and 300 g CaCO.sub.3, Up to 5 litres of water was added during the process. Regardless of the extensive dilution, the mannitol concentration reached 10.4% and lactate concentration elevated close to 5% without optimization. The hydrolysis can continue as the CBP reaction during the microbiological process.
[0068] In both Examples, the metabolites were monitored using NMR (Nucleic Magnetic Resonance) method (Laatikainen et al. 2016). These results indicated that after the completion of the mannitol process, the broth still contained glucose and mesophilic lactic acid bacteria. Their addition to the ongoing lactate fermentation in another reactor or pool could add the final yield particularly at the elevated temperature (30->37° C.).
[0069] In the mannitol process no more than 5% of the lactic acid was produced, whereas the production level in pool 1 was 9.2%. After the removal of mannitol, the residual fraction could induce higher lactate yields at 37° C. when added to pool 1 from pool 2. This could be deducted also from the relatively high level of glucose present in the broth according to the NMR (about 0.5%) in the end of the process. This indicates the potential of the microbial culture to elevate the lactate production during the remaining phase.
REFERENCES
[0070] Beckinghausen, A., Dahlquist, E., Schwede, S., Lindroos, N., Retkin, R., Laatikainen, R., Hakalehto, E. (2019). Downstream processing of biorefined lactate from lake bottom zero fiber deposit—A techno-economic study on energy-efficient production of green chemicals. 11th International Conference of Applied Energy, Västerås 12-16 Aug. 2019. [0071] Den Boer, E., Lucaszewska, A., Kluczkiewicz, D., Lewandowska, D., King, K., Reijonen, T., Suhonen, A., Jääskeläinen, A., Heitto, A., Laatikainen, R., Hakalehto, E. (2016). Volatile fatty acids as an added value from biowaste. Waste Management, 58: 62-69. [0072] Hakalehto, E. (2008). Biotechnical and microbiological production method and equipment. European Patent Application 08701690.3. [0073] Hakalehto, E. (2011). Simulation of enhanced growth and metabolism of intestinal Escherichia coli in the Portable Microbe Enrichment Unit (PMEU). In: Rogers M C, Peterson N D (eds.) E. coli infections: causes, treatment and prevention. New York, USA: Nova Science Publishers, pp. 159-175. [0074] Hakalehto, E. (Ed.) (2012). Alimentary microbiome—a PMEU approach. New York, NY, USA: Nova Science Publishers, Inc. [0075] Hakalehto, E. (2013). Interactions of Klebsiella sp. with other intestinal flora. In Pereira, L. A. & Santos, A. (eds.) Klebsiella infections: Epidemiology, pathogenesis and clinical outcomes. Nova Science Publishers, Inc. New York, USA. [0076] Hakalehto, E. (2015a). Enhanced microbial process in the sustainable fuel production. In: Jinyue, Y (ed.). Handbook of clean energy systems. Wiley JR & Sons. Inc, Chichester, West Sussex, UK. [0077] Hakalehto, E. (2015b). Hygienic lessons from the dairy microbiology cases. In: Hakalehto, E. (ed.) Microbiological food hygiene. New York, NY, USA: Nova Science Publishers, Inc. [0078] Hakalehto, E. (2016a). Microbiological surveillance methods for the industries: comments on general strategies and theoretical background. In: Hakalehto, E. (ed.) Microbiological Industrial Hygiene. New York, NY, USA: Nova Science Publishers, Inc. [0079] Hakalehto, E. (2016b). The many microbiomes. In: Hakalehto, E. (ed.) Microbiological Industrial Hygiene. New York, NY, USA: Nova Science Publishers, Inc. [0080] Hakalehto, E. (2016c). Utilization of intestinal bacteria from slaughtered animals in industrial processes and waste treatment. US Patent Application US20160251684A1. [0081] Hakalehto, E. (2018a). The effects of bioprocess scale, intracellular milieu and environmental parameters. In: Hakalehto, E. (ed.) Microbiological Environmental Hygiene. New York, NY, USA: Nova Science Publishers, Inc. [0082] Hakalehto, E. (ed.) (2018b) Microbiological Environmental Hygiene. New York, NY, USA: Nova Science Publishers, Inc. [0083] Hakalehto, E. (2020). Current megatrends in food production related to microbes. Journal of Food Chemistry and Nanotechnology 6(1): 78-87. [0084] Hakalehto, E., Hänninen, 0. (2012). Gaseous CO2 signal initiate growth of butyric acid producing Clostridium butyricum both in pure culture and in mixed cultures with Lactobacillus brevis. Can J Microbiol, 58: 928-931. [0085] Hakalehto, E., Jääskeläinen, A. (2017). Reuse and circulation of organic resources and mixed residues. In: Dahlquist, E. and Hellstrand, S. (Eds.) Natural resources available today and in the future: how to perform change management for achieving a sustainable world. Springer Verlag, Germany. [0086] Hakalehto, E., Humppi, T., & Paakkanen, H. (2008). Dualistic acidic and neutral glucose fermentation balance in small intestine: Simulation in vitro. Pathophysiology, 15: 211-220. [0087] Hakalehto, E., Heitto, A., Andersson, H., Lindmark, J., Jansson, J., Reijonen, T., Suhonen, A., Jääskeläinen, A., Laatikainen, R., Schwede, S., Klintenberg, P., Thorin, E. (2016). Some remarks on processing of slaughterhouse wastes from ecological chicken abattoir and farm. In: Hakalehto, E. (ed.) Microbiological industrial hygiene. New York, NY, USA: Nova Science Publishers, Inc. [0088] Jääskeläinen, A., Rissanen, R., Jakorinne, A., Suhonen, A., Kuhmonen, T., Reijonen, T., Antikainen, E., Heitto, A., Hakalehto, E. (2016). How Does Modern Process Automation Understand the Principles of Microbiology and Nature. 9th EUROSIM Congress on Modelling and Simulation (EUROSIM 2016) 12-16 Sep. 2016 Oulu, Finland. [0089] Laatikainen, R., Laatikainen, P., Hakalehto, E. (2016). Quantitative quantum mechanical nmr analysis: The superior tool for analysis of biofluids. In Proceedings of the 1st Int. Electron. Conf. Metabolomics, 1-30 Nov. 2016; Sciforum Electronic Conference Series, Vol. 1, 2016, C005; doi:10.3390/iecm-1-C005 [0090] Schwede, S., Thorin, E., Lindmark, J., Klintenberg, P., Jääskeläinen, A., Suhonen, A., Laatikainen, R., Hakalehto, E (2017). Using slaughterhouse waste in a biochemical based biorefinery-results from pilot scale tests. Environmental Technology, 38: 1275-1284.