A fluidized-bed combustion process with inherent CO2 separation; application of chemical-looping combustion

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Abstract

For combustion with CO2 capture, chemical-looping combustion has the advantage that no energy is lost for the separation of CO2. In chemical-looping combustion oxygen is transferred from the combustion air to the gaseous fuel by means of an oxygen carrier. The fuel and the combustion air are never mixed, and the gases from the oxidation of the fuel, CO2 and H2O, leave the system as a separate stream. The H2O can easily be removed by condensation and pure CO2 is obtained without any loss of energy for separation. This makes chemical-looping combustion a most interesting alternative to other CO2 separation schemes, which have the drawback of a large energy consumption. A design of a boiler with chemical-looping combustion is proposed. The system involves two interconnected fluidized beds, a high-velocity riser and a low-velocity bed. Metal oxide particles are used as oxygen carrier. The reactivities needed for oxygen carriers to be suitable for such a process are estimated and compared to available experimental data for particles of Fe2O3 and NiO. The data available on oxygen carriers, although limited, indicate that the process outlined should be feasible.

Introduction

It has been known for more than a 100 years that CO2 is a greenhouse gas and that the release of CO2 from fossil fuel combustion may affect the climate of the earth (Arrhenius, 1896). In the last years the concern over the effects of an increased release of greenhouse gases has been growing. The release of CO2 from fossil fuel combustion is the most important of these emissions. In the developing countries, the economic growth results in a rapid increase in the demand for energy supplied by fossil fuels, while the developed countries have not yet found the means for substantially decreasing their use of these fuels. In the future it is not unlikely that radical measures to decrease CO2 emissions will be demanded. Therefore, various options need to be investigated.

One strategy to decrease CO2 emissions is to separate the CO2 from the fuel gas and to store it. Several possibilities for such sequestration have been proposed:

Storage in used oil and gas fields: On an average, about twice as much CO2 can be stored in depleted gas fields as the CO2 obtained from burning the gas extracted from the field (Blok, Williams, Katofsky, & Hendriks, 1997). In the case of oil fields, the CO2 can be used to extend the production, the so-called enhanced oil recovery.

Storage in deep coal beds: The CO2 injected in a coal seam is absorbed in the coal and stored in its pore matrix, releasing methane trapped, which can be collected and sold (Anon, 1999). The process is called enhanced gas recovery.

Storage in aquifers: The potential storage capacity is large (Riemer, 1998). This possibility is already in use in Norway, where natural gas containing CO2 is cleaned, with the resulting CO2 injected into an aquifer 800–1000m below the bottom of the sea (Lindeberg & Holloway, 1998). In fact, one million tons of CO2 per year or 3% of Norway's total CO2 emissions are disposed in this way (Herzog, Eliasson, & Kaarstad, 2000).

Deep sea storage: At pressures above approximately 50bar, corresponding to a depth of 500m,CO2 becomes a liquid. The density of this liquid is somewhat lower than that of the surrounding seawater and in its pure form the liquid will rise slowly and ultimately reach the level where gas bubbles are formed. However, if proper measures are taken to allow the CO2 liquid to mix with the seawater, the resulting mixture obtains a higher density than the seawater and instead sinks. The storage capacity is enormous, but local effects on the environment need to be investigated.

Deep sea bottom storage: At high pressures, i.e. 3000m below the sea level, the density of pure CO2 is higher than that of seawater. Thus, CO2 released at these depths will form “lakes” on the ocean floor. The potential storage capacity is vast considering the fact that the average depth of the sea is 3700m and that more than 50% of the earth's surface is found at a depth of more than 3000m. However, local effects on the sea floor environment are obviously inevitable.

The estimated cost of CO2 disposal, e.g. 4–8 US $/ton C (Riemer, 1998), is small compared to the costs for separation of CO2, which is typically in the range 100–200 US $/ton C (Freund, 1998). Consequently, the major problem seems to be to extract the CO2 from the fuel conversion process. The available or proposed technologies all have the disadvantage of consuming large amounts of energy. The major loss in efficiency arises from the energy needed for separation of CO2 and for compression to liquid form. Typically, the energy needed for compression is about one-fourth of the total energy needed for separation and compression. For a coal-fired power plant, roughly one-fifth of the electricity produced will be lost for CO2 separation and compression (Lyngfelt & Leckner, 1999). This decrease in efficiency alone increases the cost for electricity production with one-fourth, and in addition there are costs related to separation and handling of CO2. If natural gas is used as a fuel, the relative loss in efficiency is somewhat smaller, but still substantial.

Today, power production contributes with one-third of the CO2 released from fossil fuel combustion world-wide (Herzog et al., 2000). Although the cost for separation of CO2 is substantial, power plants using fossil fuel and CO2 capture may well be the least costly alternative for CO2-free power production (Keith & Parson, 2000).

Chemical-looping combustion (CLC) offers a solution where no energy is needed for the separation. The process uses a solid oxygen carrier to transfer the oxygen from the air to the fuel. The oxygen carrier is recycled between a fuel reactor, where it is reduced by the fuel, and an air reactor, where it is oxidized by the air. Thus, the air is never mixed with the fuel, and the CO2 does not become diluted by the nitrogen of the flue gas. The outgoing gas from the reduction step will contain water vapour and CO2. The water vapour can easily be separated by condensation, and the CO2 is delivered without an energy penalty for the separation. Energy is still needed, however, to compress CO2 into a liquid suitable for sequestration.

The purpose of the present paper is to assess the potential of chemical-looping combustion — is it technically and economically realistic? In order to do this, a tentative design of the process is made. Aspects of importance for judging the realism of the process are discussed.

Section snippets

Chemical-looping combustion

Chemical-looping combustion has been discussed earlier in the literature as an alternative to normal combustion (Richter & Knoche, 1983; Ishida & Jin, 1994; Anheden, Näsholm, & Svedberg, 1995). The system is composed of two reactors, an air and a fuel reactor, as shown in Fig. 1. The fuel needs to be in a gaseous form and is introduced to the fuel reactor, which contains a metal oxide, MeO. The fuel and the metal oxide react according to(2n+m)MeO+CnH2m→(2n+m)Me+mH2O+nCO2.The exit gas stream

Reactor design

The reactors in Fig. 1 could be designed in a variety of ways, but two interconnected fluidized beds have an advantage over alternative designs, because the process requires a good contact between gas and solids as well as a flow of solid material between the two reactors.

The system proposed is a circulating system composed of two connected fluidized beds, a high-velocity riser and a low-velocity bubbling fluidized bed (Fig. 2). The bed material circulating between the two fluidized beds is the

Oxygen carriers

The metal oxide, used as an oxygen carrier in chemical-looping combustion, must have sufficient rates of reduction and oxidation, at the same time as it possesses enough strength to limit particle breakage and attrition. It is also an advantage if the metal oxide is cheap and environmentally sound. A number of metals and their corresponding oxides have been mentioned in the literature as possible candidates: Fe, Ni, Co, Cu, Mn and Cd. At Tokyo Institute of Technology, Ishida and co-workers have

Theory

Assuming that the fuel is completely burnt, the fuel consumption is given by the heating value of the fuel, Hi, and the fuel power, Pfuel:ṁfuel=PfuelHi.The amount of oxygen needed for oxidation of the fuel is thenṁo=MO2ṁfuelMfuelSr,where Sr is the stoichiometric ratio for the reaction between fuel and oxygen, and Mi denotes the molar mass of species i. The air ratio, λ, is given by the volume fraction of oxygen in the air from the oxidizer, xO2,exλ=0.21(1−xO2,ex)0.21−xO2,ex,where 0.21 is the

Design criteria

Design criteria were chosen for the layout of an atmospheric boiler with a power of 10MW. Such a boiler is suitable for the demonstration of the technology and for obtaining data and experience of the process in a semi-commercial scale. The boiler could be used for heat production, for district heating or for industrial process steam. As seen in Fig. 2, the design resembles that of a circulating fluidized bed (CFB) boiler for combustion of solid fuels, thus using elements of proven technology.

Results and discussion

Eqs. (3)–(20) together with the values of Table 3, Table 4 give the results presented in Table 5. The required conversion rates of the oxygen carriers were 9%/min in the oxidizer and 3%/min in the reducer and the required mass flow of solids between the two fluidized beds is approximately 50kg/m2s. These results are realistic judging from the experimental data, as will be discussed below.

The reactivity of the carrier can be expressed in terms of conversion rate. The conversion rates, rox and r

Conclusions

A design of a combustor based on chemical-looping combustion with two interconnected fluidized beds is proposed. The required reactivities of oxygen carriers, suitable for such a process, are estimated. It is concluded from the limited experimental data on oxygen carriers available in the literature that the process outlined is realistic. Firstly, the reaction rates for both reduction and oxidation are sufficient in terms of the bed masses needed. This means that the dimensions of the reactors,

Acknowledgements

This work has received financial support from the Swedish National Energy Administration (Energimyndigheten), the School of Environmental Science at Chalmers University of Technology and Ångpanneföreningen's Foundation for Research and Development.

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