Supercritical water processes: future prospects
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Supercritical water processes: future prospects María José Cocero. High Pressure Processes research group. Department of Chemical Engineering and Environmental Technology. Valladolid University. 47011 Valladolid (Spain). [email protected] Abstracts This contribution examines the challenges faced by supercritical water processes for industrial development. As an alternative, the intensification of the supercritical water processes is presented in order to reduce the size of the equipment needed and to facilitate the scaling up of the process. The perspective of developing micro combustors using hydrothermal flames as the internal heat source could open up an alternative for the in-situ energy generation in biorefineries, for example. The fundamental studies about supercritical water hydrolysis using ultrafast reactors has enabled extremely high selectivity in the biomass fractionation processes, and in the production of C2 and C3 building blocks from key components. The high-energy consumption of this process is another issue that limit its commercialization. In the examples proposed, the energy, work recovery and energy integration allows the reduction of the total energy consumption and, in some processes, the availability of extra energy as heat and work. Key Words: Process intensification, micro combustors, oxidation, hydrolysis, shaft work, energy integration. 1 Current State Supercritical water (SCW) has been used as coolant in nuclear reactors for many years. In addition, geothermal studies about the water inside the earth’s crust have
contributed knowledge to the hydrothermal processes [1]. Modell had the vision to develop industrial processes based on the use of water at supercritical conditions after the preliminary studies about the total miscibility of hydrocarbons in SCW [2]. His companies Modar inc and Modell were a key point in the development of the supercritical water oxidation processes for environmental applications [3]. In its origin, the process aroused a great interest among the process industries or in public organisms as being a solution to recalcitrant waste treatment problems. Companies such as General Atomics or Foster and Wheeler were involved in the development of the supercritical water transpiring wall reactor. They made relevant contributions, working in projects for public USA organisms, to the development of injectors to achieve good mixing [4]. In Europe, Franck significantly improved the available information regarding SCW properties [5-7]. Companies such as Chematur built the first sludge SCWO pilot plant with a treatment capacity of 200 kg/h, in 1998 [8]. In Spain, the EMGRISA public company supported Valladolid University’s research to develop the first cooled wall reactor in a pilot plant with a treatment capacity of 30 kg/h in 1994, and a demonstration plant with a treatment capacity of 200 kg/h in 2002 [9]. The main industrial development associated with sludge treatment has involved tubular reactors [10-12]. Conventional reactors are thin tubes about hundred meters long, with mixing problems that force them to work with great excesses of oxygen and with evident plugging problems due to solid precipitation. In practice, industrial plants work with two reactors, one under operation and the other undertaking the cleaning of deposited solids [13-15]. In some applications, the changeover of the reactors takes over 30 minutes. Furthermore, cleaning is a highly energyand time-consuming step. Its industrial development has not progressed due to the lack of control of corrosion and salt precipitation processes, the high reactor surface exposed to corrosion and the
small diameter that favors plugging problems, in addition to the high processing cost [16-18]. A well-known problem of SCW oxidation is the energy requirement, which can be very high, particularly, if simple plug-flow tubular reactors are used, inasmuch as these designs require the preheating of the influent up to supercritical water temperature. The correct use of the energy produced by the oxidation is a crucial step in order to make SCWO processes economically viable [19-21]. SCW gasification is another technology to which important research efforts have been devoted, but it has not been possible to progress. Only one demonstration industrial scale plant Hydromethans AG is in Switzerland [22]. Kruse concluded in a recent review that the main reason why a SCW gasification process is not attractive for industry today is due to the high processing costs [23]. Only biomass with high disposal costs are considered to be interesting feedstock, such as sewage sludge. Kruse identified the same problems found in the SCWO: plugging, corrosion, reactor design and material selection. As possible future developments, Kruse proposed hydrothermal gasification as part of a bio-refinery. During hydrothermal liquefaction, a tarry oil and an aqueous phase are produced. So, It was then proposed to gasify the organic compounds in the aqueous effluent, and use the hydrogen to up-grade the oil [23-25]. More recently, material synthesis in SCW is a technology which is approaching the market. Adschiri has produced different materials for new industrial developments [26]. Lee had a demonstration plant under operation which synthesized nanoparticles by using SCW [27]. In recent years, Lester has coordinated the Shyman EU project for the development of a 1000 ton/year demonstration plant producing nanomaterials [28-29]. Again, this technology has not reached the industrial development that it could achieve, due to the high processing cost. In addition to the energy consumption, the effluent particle concentration is very low, and the water has to be eliminated, so the downstream processing could require a lot of both, time and energy. In the cases of
many materials that have been developed, the cost is much higher than the same materials that are produced by conventional technologies. The opportunity, now, lies in developing new materials that can not be produced by conventional technologies, or that would be more expensive to produce conventionally. In this special issue, Adschiri [30] and Aymonier [31] illustrate the interest of this technology for the production of advanced nanostructured materials and for developing new nanotechnology applications. The petrochemical companies are studying the upgrading of heavy oil by SCW. This process takes advantage of the low dielectric constant of water, which allows hydrocarbons’ solubility. In addition, temperature and pressure can be manipulated to adjust the water’s ionic product creating a highly ionic medium, with high [H+] concentration that could improve the hydrolysis [32]. Although many studies have not been published, relevant manuscripts about thermodynamics, kinetics, and experimental and theoretical developments on the phase equilibria of relevant water– hydrocarbon systems are available [33-35]. The advantage of this process over other upgrading technologies is the high process intensification that can be achieved by the use of SCW. Regarding energy production, power plants with SCW steam generators as the Benson type are conventional. [36-37]. Also novel SCW reactors are considered more efficient reactors for nuclear plants [38]. 2 SCW processes Challenges The strong features of the supercritical water processes lie in the knowledge of the processes fundamentals supported by the abundant research SCW. Specifically: the SCW properties and its mixtures; thermodynamic and kinetic studies; thermodynamic modelling; and the computational fluid dynamic model designed to improve the hydrodynamic reactors behavior. Operation at high temperature could mean fast reaction kinetics, which could allow extremely fast processes to be developed.
The weak features include the high processing cost, in addition to the operational problems associated with plugging, corrosion, reactor design, dilution of the effluents, and high energy consumption. The processes have high costs, and this in turn has an important impact on the high cost of products. From my point of view, the main challenges concerning SCW industrial implementation are: To reduce the cost of the processes, by reducing the cost of equipment. To reduce the operation cost by improving the heat and work recovery and the integration of the energy, to reduce the overall energy consumption. To improve technical issues regarding operations with solids at a high temperature and pressure, pumping highly concentrated solid suspensions, minimizing the abrasion of valve stems, and improving the solid output from SCW reactors. To implement downstream processes in order to achieve marketable products. 3 SCW process perspectives. One way to reduce equipment costs is to take advantage of the SCW process’s fast kinetics to reduce reaction time, which will reduce the reactor size. By reducing the residence time from 10 minutes to milliseconds, it is possible to change conventional reactor volumes of m3 for reactors with volumes of dm3. That means reducing the reactor size, thus facilitating the scale-up of the process as well as the reactor control. In some applications, it is possible to improve the reactor’s design to reduce the problems associated with operations involving solids at a high pressure and temperature. It is possible to reduce the operation cost by improving the energy and work recovery, for example, by recovering the work associated with the depressurization, and implementing energy integration [39].
The processes should be focused on obtaining products that are closer to the market. As there is much information about process fundamentals, the research should be oriented to develop “products close to the market”. If it is the case that the process fundamentals are not yet well known, our first step is to improve our knowledge of the process fundamentals in order to achieve a faster way of developing new processes and new products. In this section, the perspectives of the development of three supercritical water processes are presented. These processes can operate with residence times of milliseconds, which could achieve a high level of process intensification. The energy and work recovery, as well as the energy integration, are taken into account in order to minimize energy consumption or even produce net energy as heat and shaft work. 3.1 Micro-combustors operating on the intensification of the supercritical water oxidation process, using hydrothermal flames as the internal heat source. In 1988, Schilling and Franck achieved the formation of a diffusion flame in homogenous supercritical aqueous fluids. The combustion of 30% methane with oxygen in the homogenous supercritical phase was investigated, and stationary diffusion flames were generated up to pressures of 2000 bar and temperatures of 500 ºC [40]. At that time this was a considered a scientific curiosity, but nowadays the effect of operation conditions on the ignition temperature has been studied in order to achieve stable mixing and diffusional hydrothermal flames [41-44]. Usually a flame is defined as the visible part of the combustion reaction and consists of a surface where reaction occurs. This surface separates the oxidant from the fuel (in the case of diffusion, non-premixed, flames) or it separates the reagents from the reaction products (in case of premixed flames). The surface moves towards the reagents with a flame front velocity. If this velocity is the same as the fluid velocity, the flame will remain stationary. If flow velocity is higher or lower than flame front velocity, the flame will be blown away from the tube or it will move against the flow, resulting in
backfire, respectively [45]. See figure 1 for simulation contours of a hydrothermal flame. It is possible to operate with ignition temperatures of between 400 and 500ºC, and residence times between 10-100 ms. The flame ignition is affected by fuel, oxidant, ratio of fuel/oxidant and the geometry of the injection system [46-50], and it is possible to develop processes that support hydrothermal flames as the heat source [36,41]. Although the reactor effluent energy can be recovered by a Rankine Cycle, the process is still highly energy demanding. Additionally, oxygen is the most commonly used oxidant in order to reduce the air compressor energy consumption. The implementation of hydrothermal flames as the internal heat source in the supercritical water oxidation processes opens up the opportunity for the SCWO to achieve an energetically selfsufficient process, and to produce energy [51]. Figure 1. Flame simulation contours of new cooled wall reactor with two outlets: (a) IPA mass fraction, (b) reaction rate [52]. The SCWO processes with hydrothermal flames have a number of advantages over the flameless processes. Some of these advantages could overcome the traditional challenges that make a successful and profitable commercialization of SCWO technology difficult. The advantages include the following [52]: • The reduced residence times (in the order of milliseconds) encourage the construction of smaller reactors (micro-combustors).
• It is possible to carry out the reaction with feed injection temperatures near to room temperature when using vessel reactors [48,53]. This avoids problems such as plugging and corrosion in the preheating step, which is an advantage from the perspective of operation and energy integration. • Higher operation temperatures improve energy recovery. The extremely low residence time allows micro reactors to be developed as an alternative to the long tubular reactors. The strong reduction of the ignition temperature with pressure will allow the operation at temperatures of 600-650ºC. At those conditions the SCW oxidation achieves a higher efficiency than at lower temperatures. The operation temperature can be even higher if the work recovery required a vapor at a higher temperature. As the reactor size decreases significantly, the operation with air as the oxidant could be a more economical alternative. On an industrial scale, it could also be possible to implement oxidation with air, as opposed to the conventional SCW facilities that operate with cryogenic oxygen [51]. When direct expansion of the effluent is used, the energetic efficiency is much higher than when the effluent is used to heat an auxiliary fluid of a Rankine or Brayton cycle. We have calculated that it is possible to operate with air as the oxidant, or to use enriched air through the direct expansion of the effluent in a turbine, and thus produce net energy [51-53].
Figure 2. UVa two-outlet reactor for energy production. Details of construction can be found in literature [53]. Figure 3. SCWO scheme, designed to operate with a direct effluent reactor expansion in a turbine. Even when the option of direct expansion of the effluent is, by far, the most energetically efficient, it will be not applicable in the short term. This is mainly due to the fact that the composition of the effluent (50-80 % mol of water, carbon dioxide and nitrogen if air is used as oxidant) makes it unsuitable for expansion in a conventional turbine. This composition places the effluent somewhere between the pure water used in the steam turbine, and the flue gases, which are products of combustion used in gas
to develop the downstream processes for concentrating/separating the effluent, thus producing the final products. The SCW hydrolysis of biopolymers, such as cellulose, opens a new route for developing new products that cannot be obtained by the conventional acid or alkaline hydrolysis. Biomass with a high cellulose concentration could be a raw material for producing cellulose with different molecular weight and properties, with new market opportunities. Although research is needed to improve the fundamental knowledge of biomass SCW hydrolysis, the first SCW hydrolysis process, called the Plantrose process, developed by Renmatix, is running in a demonstration scale in Georgia, USA [69]. 3.3 Supercritical water as a reaction media to produce building blocks The SCW can be used as a reaction medium to produce chemical compounds with high selectivity. The selectivity is improved by controlling the ion concentration in order to avoid ionic reactions. This has been presented in the case of cellulose hydrolysis. The glucose and fructose kinetic and reaction mechanism studies have allowed us to determine reaction paths for obtaining the selection of glycolaldehyde (building block compound made up of two carbons) or pyruvaldehyde (building block compound made of three carbons). The reactions were assumed to follow the reaction pathway shown in figure 6.
Figure 6. Reaction pathway of glucose and fructose hydrolysis in supercritical water. This reaction pathway was built following the schemes developed in reference [70]. The reaction of glucose isomerization occurs through ring opening and keto–enol tautomerism. These reactions form transition states with OHor H+ ions. Also, fructose dehydration forms transition states incorporating H+ ions (one per H2O molecule lost) [71]. The production of glycolaldehyde was enhanced at supercritical conditions because the OH-/H+ concentration is highly decreased and so is the concentration of fructose and its derived products. Fructose can follow two main reaction pathways: fructose dehydration or retroaldol condensation and a second reaction to form glyceraldehyde as the main product from fructose [65, 66]. Results show that fructose can be selectively transformed into pyruvaldehyde, at 400ºC and 23 MPa with a yield of 89% w·w-1 without using any catalyst, and with a residence time of 0.7 s [72]. The hydrolysis of glucose to glycolaldehyde was achieved at 400ºC and 23 MPa with a residence time of 3 s; glycolaldehyde selectivity at those conditions was 75% w·w-1 [73]. The reactions of fructose were analyzed in combination with glucose. It was determined that different retro-aldol condensation products can be obtained depending
on the starting material. Fructose produces mainly C-3 molecules (pyruvaldehyde) and glucose produces mainly C-2 molecules (glycolaldehyde). The isomerization of fructose to glucose is negligible, and so is the production of C-2 when the starting material is fructose. The non-ionic medium induced at supercritical water conditions significantly improves the selectivity, favoring the retro-aldol condensation of glucose instead of isomerization or dehydration. Organic chemistry has developed systematic mechanisms to produce many chemical products from oil. These reactions are founded on simple molecules, such as ethene, propene or benzene, with the addition of functional groups. In the oil industry, chemical processes require multiple steps, the use of solvents, catalysts and excessive energy, which have environmental incompatibilities. In the bio-based chemical industry, key compounds are more complicated molecules with highly functional groups, such as glucose for example. Now, a new systematization of organic chemistry for the removal or rearrangement of the functional groups has to be developed. The chemical processes must include simplified steps and improved process intensification in order to achieve a sustainable process from biomass. 4 Concluding remarks, and identification of the research needed for the development of the intensification of the sustainable supercritical water processes. The SCW processes have been devoted to important, marketable research efforts, but it has not been possible to achieve the industrial development that was expected. Among the reasons for this problem are the high processing cost, and the difficulty of operating with solids at a high pressure and temperature. Taking into account the SCW properties as the reaction media, the SCW process intensification is presented as an alternative for developing an ultrafast process that allows a reduction in the reactor cost. Work recovery, heat integration and heat and shaft work production are considered to minimize energy consumption or even produce net energy.
The intensification of the SCW oxidation process by using hydrothermal flame as an internal heat source is presented as an alternative for developing micro combustors. The expansion of the effluent in a turbine could be the way to produce in-situ energy for biorefinery development. Our preliminary results concerning the SCW oxidation reactor with the hydrothermal flame as the internal heat source indicated that it would be possible to produce energy by expanding the SCW oxidation reactor effluent in a turbine. To develop this process, some research needs could be summarized as follows: New studies to develop stable hydrothermal flames from different compounds, mainly biomass from different origins, and to establish the methodology for calculating them. To improve the reactor’s design and reduce the plugging problems, taking into account its operation with solids at a high pressure and temperature, and to develop new construction materials to control the corrosion and reduce the equipment costs. The work and energy recovery have a key relevance, due to the high temperatures and pressure effluents and the process high energetic consumptions. Therefore it is necessary to develop new turbines that can operate with the SCW oxidation effluents to recover the work. To study technical issues concerning the expansion of two phase streams in order to implement the direct expansion effluents. The SCW ultrafast hydrolysis is presented as an alternative for developing sustainable biorefineries. The SCW media properties allow it to operate mainly by ionic reaction mechanisms at subcritical water, and by radical reactions mechanism at SCW. The operation with ultrafast micro reactors has remarkably increased the selectivity. The fundamental knowledge about the reaction mechanism and the effect of SCW properties are a key point in achieving this selectivity.
This implies that future research about the reaction mechanism must be carried out in continuous reactors in order to obtain accurate data. The heating and cooling steps should be taken into account to avoid degradation, and to control the residence time. The operation with solids at a high pressure and temperature has to be considered in all the process steps. In the same way, high pressure view-cells used in solubility and phase behavior studies on biomass hydrothermal reaction require that the preheating time be avoided, since the dissolution/hydrolysis step could be extremely fast and thus take place during the preheating. Therefore, continuous flow cells, or those provided with a system for solid injection, will be the most widely used. The application of the SCW intensified process required commercial equipment to operate continuously with low residence times. In fact, the commercial equipment itself, even a lab scale commercial suspension pump equipped with valves that avoid plugging due to suspension particles, is needed. Technicians with the experience to implement this commercial equipment in the research lab are also needed. In addition, even when the components of biomass are alike, each biomass presents its own peculiarities. Thus, one must study new local biomass sources to achieve specific chemicals and energy. Knowledge mechanisms based on SCW hydrolysis, such as the SCW ultrafast hydrolysis, are proposed in order to obtain selective building blocks. Two examples for producing highly selective C2 and C3 building blocks from fructose and glucose are presented as an alternative to the production of selective chemicals by the intensified SCW hydrolysis process. Research requires organic chemistry to allow the elimination and rearrangement of functional groups from the building blocks produced, whereas chemical engineering enables the development of simplified and compact
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