CArbon-free Electricity by SEWGS: Advanced materials, Reactor and process design
STICHTING ENERGIEONDERZOEK CENTRUM NEDERLAND
1755 Le Petten
€ 1 117 854
Sort by EU Contribution
AIR PRODUCTS PLC
€ 100 000
BP EXPLORATION OPERATING COMPANY LTD
€ 148 924
POLITECNICO DI MILANO
€ 242 400
€ 654 337
Grant agreement ID: 213206
1 January 2008
31 December 2011
€ 3 143 422
€ 2 263 515
STICHTING ENERGIEONDERZOEK CENTRUM NEDERLAND
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Final Report Summary - CAESAR (Carbon-free Electricity by SEWGS: Advanced materials, Reactor and process design)
The sorption enhanced water gas shift (SEWGS) process is a technology which is very attractive for removing CO2 from a natural gas or coal and derived syngas. The process utelises multiple vessels filled with catalytically active carbon dioxide (CO2) adsorbent. When syngas (containing CO, H2, carbon dioxide (CO2) , H2O, and inerts) is fed at high temperature and pressure ( 400 ºC, 25 bar), CO2 is removed by the sorbent. Hence, the WGS equilibrium is shifted towards complete conversion of CO, thereby maximizing the production of H2 and CO2. The simultaneous removal of CO2 yields an essentially carbon-free, high temperature, high pressure, hydrogen rich product stream.
The SEWGS process consists of a number of packed bed vessels operating in a pressure swing cycle and the carbon dioxide (CO2) sorbent is periodically regenerated by purging with steam at low pressure. The full SEWGS process had first been demonstrated on a 25 kWth scale (0.06 tonne carbon dioxide (CO2) per day) in ECN's lab in a multicolumn test rig for thousands of CO2 adsorption/desorption cycles within the EU Sixth Framework Programme (FP6) project CACHET. However, techno-economic assessments for the NGCC application showed that a substantial cost reduction was needed to make the technology competitive with post combustion capture.
In the Seventh Framework Programme (FP7) project CAESAR, Air Products, BP, ECN, SINTEF and Politecnico di Milano worked together the past 4 years in the further development of the SEWGS process with the objective to reduce the energy penalty and the costs of CO2 avoided to less than EUR25/ t CO2 through optimization of sorbent materials, reactor and process design and smart integration of the SEWGS unit in a combined cycle power plant. The efficiency penalty is an important contributor to the capture costs, and in this, steam use for the regeneration of the sorbent is a significant determining factor in the efficiency penalty. The cost target of 25 EUROS can be translated into a requirement for an overall steam/CO2 ratio of less than 2 mol/mol, which is a factor 2 lower than 4 mol/mol ratio for the sorbent available at the start of the CAESAR project, i.e. with the CACHET sorbent.
In the first years considerable efforts were made in testing over 400 different sorbents finally leading to new patented CO2 sorbent (called ALKASORB). Long term testing showed the stability of the working capacity as well as the mechanical stability of ALKASORB during 5000 cycles at a minimum steam/CO2 ratio (less than 2 mol/mol). For cycle optimization and to study different plant lay outs i.e. vessel size, vessel number, regeneration medium, pressure etc. a dedicated SEWGS model was developed. Optimization studies with this model provide insight in ways to improve the SEWGS process on both a technical and ultimately economic basis.
Further, it has been demonstrated that the ALKASORB sorbent is catalytically active for the water-gas shift reaction and therefore, the SEWGS process does not require a separate shift catalyst, which also brings substantial economic and technical benefits. ALKASORB also captures H2S along with the CO2 without significant loss of capacity. This is an advantage for both the IGCC and the blast furnace applications.
The most promising applications for the SEWGS technology are IGCC power plants and power production from blast furnace top gas. For the IGCC application, the techno-economic assessments showed that the SEWGS technology with the ALKASORB sorbent is a cost effective CCS solution with a 15% capture cost reduction (36EUROS/t CO2 versus 31EUROS/tCO2 ) compared to conventional technology (i.e. Selexol) and a 30% lower energy use per ton of CO2 avoided (3.67 versus 2.49 MJLHV/kg CO2). SEWGS reduces investment and also the fuel cost due to the co-capture of sulphur and consequent equipment costs savings, and higher efficiency.
At the end of the third year, the consortium partners evaluated the SEWGS technology using NASA's technology readiness level methodology and concluded that SEWGS is currently on level 5 to 6 and from a technical point of view and ready to move to the next development level, which is a pilot plant installation with a capacity of 35 ton CO2 per day. This is 200 times larger than the current ECN's multi column SEWGS installation, but still 100 times smaller than an envisaged commercial scale installation.
However, despite the 30% lower energy use per ton of CO2 avoided, the calculated 15% cost reduction was not yet sufficient to justify further scale up of the technology and investments in a pilot plant installation. The assessment studies indicate that an increased sorbent capacity of 50 to 100% would result in capture cost advantage of 30 to 40%. Therefore, in the final year of CAESAR, some additional effort was focused on achieving such a breakthrough in sorbent capacity.
The additional sorbent development work during the last year of the CAESAR project indeed resulted in a new, improved sorbent called ALKASORB+ with a substantially higher capacity with benefits on capture cost. With the new ALKASORB+ sorbent, the cost of CO2 avoided for the IGCC application is reduced to approx. 23EUROS/t CO2 which is a reduction of almost 40% compared to the SELEXOL capture case. Since ALKASORB+ requires much less steam, the specific energy consumption is substantially reduced to 44% below the specific energy consumption for the Selexol (2.06 versus 3.67 MJLHV/kg CO2).
With this breakthrough in sorbent capacity, the SEWGS technology is now ready for scale up to a pilot unit capturing 35 ton CO2 per day. This pilot plant will prove the technology under field conditions and at a sufficiently large scale to enable further up-scaling; delivering both the basic design and investment costs of a full scale SEWGS demonstration plant.
Project context and objectives:
CAESAR: Carbon-free electricity production by SEWGS: Advanced materials, Reactor and process design.
The overall objective of the CAESAR project was: Reduction of energy penalty and costs of the SEWGS CO2 capture process through optimization of materials, reactor- and process design. At the start of the project, the consortium emphasized that with an optimized SEWGS process CO2 capture costs could be reduced to less than 15 Euro per ton CO2. The efficiency penalty is an important contributor to the capture costs and the steam use in the regeneration of the sorbent is a determining factor in the efficiency penalty. So the cost target was translated into a requirement for the overall steam/CO2 ratio of 2 mole/mole, compared to a ratio of more than 4 mole/mole at the start of the project.
The project focused on the application of the optimized SEWGS process for pre- combustion CO2 capture from natural gas fuelled power plants but also looked into the possible application of the SEWGS process in IGCC power plants fed by coal or refinery residues and the off-gas of blast furnaces in the steel industry. Finally, the project aimed on the development of a design package for a SEWGS pilot plant. Subsequently, in further projects (not part of the current CAESAR proposal) this pilot plant can be built as a step up to industrial application of the SEWGS process. CAESAR builds on the SEWGS development of the FP6 integrated project CACHET The emphasis in the FP6 project CACHET was placed on demonstrating the SEWGS process on a larger scale and building a continuous, multi-bed SEWGS process demonstrator. Most of the man months and funds in CACHET went into the construction of the single-column test unit, long term sorbent testing in the single column, and process demonstration in the multi-column test unit. CAESAR used both these test rigs in order to bring the SEWGS process a big step closer to the market.
Objectives and work
The general CASEAR objective has been translated into several operational objectives for the different components of the SEWGS process:
WP1 (Materials development): In this WP the consortium developed a optimum sorbent/catalyst system for application in SEWGS based on syngas from natural gas, coal, refinery residues, or blast furnace gas feeds. A minimal steam use for purge and rinse flows (in total less than 2 mol steam / mol CO2) was the main target and has been realised.
WP2 (Preliminary reactor design): In this WP the consortium developed a SEWGS reactor model that was validated against experimental results of the single column unit. For this, more than 2000 cycles of stable operation at steam to CO2 ratio of less than 2 and capture ration of more than 95% CO2 capture have been have been executed.
WP3 (Advanced reactor design): Incorporation of the developed SEWGS cycle model in the in house modelling tool SIMPAC of Air products and experimental validation on the multi-column set-up was the main objective. Subsequently, this model was used to develop a SEWGS optimised process cycle, with a total steam/CO2 ratio of 2 or less. Next the cycle was experimental demonstrated in the multi-bed SEWGS test rig. Also the cyclic SEWGS process for application in coal gas and blast-furnace gas has been development and demonstrated.
WP4 (Application and process integration): The objectives here was the development of flow sheet models and costing tools for the new SEWGS set-up for natural gas fired power generation and for coal gas and industrial applications (refinery residues gasification and blast-furnace gas).
WP5 (Process scale-up): Delivered a mechanical reactor design for a pilot plant for one of the applications studied. Results have been used in the application in the 2011 call of the RFCS for a pilot demo project of the SEWGS technology for decarbonising blast furnace gas.
WP6 (Project management and dissemination): Work resulted in public reports, peer-reviewed papers and the organisation of the EU CCS conferences (in collaboration with other FP7 projects in the CO2 capture field).
The overall objective of the CAESAR project was: Reduction of energy penalty and costs of the SEWGS CO2 capture process through optimization of materials, reactor- and process design. It is emphasized that with an optimized SEWGS process CO2 avoidance costs could be reduced to less than 15 Euro per ton CO2. The efficiency penalty is an important contributor to the capture costs and the steam use in the regeneration of the sorbent is a determining factor in the efficiency penalty. So the cost target was translated into a requirement for the overall steam/CO2 ratio of 2 mole/mole, compared to a ratio of more than 4 mole/mole at the start of the project. The general objective is translated into several operational objectives for the different components of the SEWGS process.
The CAESAR project focused on the application of the optimized SEWGS process for pre- combustion CO2 capture from natural gas, but looked also into the possible application of the SEWGS process in IGCC power plants fed by coal or refinery residues, and blast furnace top gas in the steel industry.
WP1 (Materials development)
The objective of this WP is to develop an optimum sorbent/catalyst system for application in SEWGS based on syn gas derived from natural gas, coal, refinery residues, or blast furnace gas feeds. Based on the results of a previous Sixth Framework Programme (FP6) project on the SDEWGS development a minimal steam use for purge and rinse flows of in total less than 2 mol steam / mol CARBON DIOXIDE (CO2) and a sorbent lifetime of more than 3 years are the main development targets in the sorbent material development in the CAESAR project.
- Sorbent: chemically resistant, mechanically stable, minimized steam use on regeneration compared to standard K-HTC (proof at least 2000 cycles stable operation at steam/CO2 ratio of less than 2).
- Catalyst: Stable catalyst/support under operating conditions, especially under minimal steam (proof at least 2000 cycles stable operation).
In the search for new or improved sorbent material two parallel development routs were followed:
- The first route was focused on improving both chemical as well as the mechanically stability of while minimising the steam use on regeneration of promoted hydrotalcite (K-HTC).
- The second route focussed on screening of new alumina based sorbent by using high by using high throughput techniques.
Improving the performance of promoted hydrotalcite (K-HTC) sorbent.
The CO2 sorbent used at the start of the project i.e. promoted hydrotalcite (K-HTC) showed unexplainable behaviour in the CO2 sorption cycle and in the regeneration of the sorbent with steam.
This reference hydrotalcite sorbent (denoted as K-MG70) showed poor mechanical stability and increased CO2 slip during long term testing under realistic conditions. It turned out that this was caused by the MgCO3 formation which is a slow process. A new HTC sorbent with a lower Mg content (K-Mg30) was selected for long term testing in the single column unit. During bench testing this K-Mg30 (called ALASORB) sorbent showed good capacity so this sorbent was selected for long term testing in the single column unit (See WP2 results). Although, the ALKASORB sorbent showed good overall performances, the techno-economic assessments showed that sorbent cyclic capacity must be increased with at least 50% (compared to the capacity of ALKASORB) with at least 50% in order to make the SEWGS process substantially cheaper than the more conventional capture technologies. In the final year, sorbent development resulted in a major breakthrough with respect to sorbent capacity. This ALKASORB+ sorbent has a 90% higher CO2 capacity compared to ALKSORB and also uses less steam for the regeneration. Cost calculations performed (see showed that with the new sorbent, SEWGS can capture CO2 at a price of around 25 Euro per ton CO2 avoided (see WP4 results).
In conventional shift applications, the catalyst operates under reducing conditions. For application in a SEWGS process the catalyst should be able to withstand the oxidising conditions during the cycle, such as during the sorbent regeneration by steam. It should also remain active at the SEWGS operating conditions where only a limited amount of steam in the feed is present. According to the work plan, commercially available catalysts on supports were to be benchmarked at different temperatures and in the presence of actual CO2 sorbents. However, during breakthrough experiments with promoted hydrotalcite under realistic conditions it was observed that even in the absence of a catalyst the carbon monoxide in the feed gas was completely shifted to carbon dioxide. A stability test showed the stability of the sorbent working capacity as well as shift activity during 2000 cycles, at a minimal steam to carbon ratio (2 mole/mole). Hence, it was demonstrated that the SEWGS process does not require a shift catalyst, which brings substantial economic and technical benefits.
CO breaks through almost simultaneously with CO2. Apparently, the sorbent is active for the shift reaction. After breakthrough conversion is 44%, which is somewhat below thermodynamic equilibrium. Shift activity before breakthrough is relevant for the SEWGS process.
High throughput testing of new sorbents
In total 432 new sorbent formulations have been prepared, partly characterized and more than 300 sorbents have been evaluated under realistic conditions in a three cycle adsorption-desorption test. From the evaluation, a comparison with the existing state-of-art sorbents has been made, and four leads have been selected for up-scaling and testing for sorption performance and particle stability under SEWGS conditions. However, none of these four sorbents performed sufficient to scale up the sorbent for testing in the single-column and multi-column test rigs.
WP2 Preliminary reactor design
The objectives of Work Package 2 are:
- The development of a SEWGS reactor model that is validated against experimental results.
- 2,000 cycles of stable operation of the single column unit at a steam/CO2 ratio of less than 2 mole/mole and more than 95% CO2 capture.
WP2 aimed at designing reactors for the SEWGS process. The work involved development of a model of the SEWGS process, which incorporated chemical kinetics, mass and heat transfer. Modelling was based on input from experiments on the single-column process development unit (PDU) built in the CACHET project. The model was used to design a SEWGS reactor. For applications in syngas from coal- or oil residue gasification, CO concentrations are relatively high, which means that the temperature increase due to the WGS reaction is also higher. For these applications the use of heat integrated reactors may be necessary. The task of modelling was assigned to Air Products, and the execution of experiments in the PDUs to ECN.
- Sorbent material, chemically resistant, mechanically stable, minimized steam use on regeneration compared to standard K-HTC developed and test in the single column test rig
- Creation of an experimentally validated single-column sorption-reaction model
- Publication on reactor modelling
- Publication on single-column experimental work
- Evaluation of alternative reactor designs for the SEWGS process
Performance differences single-column vs. multi-column rig
In the CACHET work, it was found that the results obtained for the SEWGS cycle in the multi-column rig was inconsistent with data collected in the single-column rig. The purpose of this task is to run experiments in the single-column to reconcile some of the differences between how these two units were operated and how much this may have contributed to the differences in performance. For example, the multi-column tests in CACHET were run at a higher purge pressure than in the single-column rig. It is difficult to reduce the purge pressure in the multi-column so additional single-column tests were run at higher purge pressure to see what effect this has on performance. The work led to identification of the most important factors that contributed to the differences in observed performance, and as such, the performance differences were resolved. As a consequence, we are able to predict the performance in the multi-column test rig from the observations in the single-column test rig, provided that the same cycles are applied in both test rigs.
Single-column PDU testing
The ALKASORB sorbent was tested under different process conditions to determine heat and mass transfer parameters for the sorption/reaction rates. All tests were performed in the absence of a separate water-gas shift catalyst. From breakthrough experiments at various CO2 partial pressures, the adsorption isotherms could be approximated. Comparison of the adsorption isotherms showed that ALKASORB has a higher capacity than the sorbent tested previously. Furthermore, adsorption isotherms in the absence and in the presence of steam were measured and compared, indicating that steam may have a detrimental effect on the CO2 adsorption capacity.
The catalytic activity for the water-gas shift reaction had been measured for both the ALKASORB and the previous sorbent, showing a markedly improved activity for ALKASORB. Small scale tests had indicated that the water-gas shift activity of ALKASORB may even be sufficient to leave out the separate water-gas shift catalyst in a SEWGS reactor if the syngas contains 200 ppm H2S. This was confirmed by performing breakthrough tests in the single-column test rig packed with sorbent in the absence of a catalyst, feeding a mixture of CO2, CO, H2 and H2O, without H2S. Full CO conversion is obtained until CO2 and CO started to break through simultaneously.
Cyclic experiments in the SC set-up were also run in order to be able to validate the reactor model. The long-term mechanical as well chemical stability of the sorbent was determined. This information was used to screen ALKASORB before it was tested in the multi-column in Work Package 3. It was demonstrated that the sorbent remained mechanically and chemically stable during operation of at least 1200 adsorption – desorption cycles. The cyclic capacity of ALKASORB was 27% higher than the cyclic capacity of the reference sorbent, which was used in CACHET. Moreover, 36% less steam was required for its regeneration. The sorbent pellets also had a 65% higher crush strength than the reference sorbent. Contrary to the reference material, the novel material did not form notable amounts of MgCO3 under relevant operating conditions. Due to the absence of this slow CO2 uptake process, the sorbent remains mechanically stable, the cyclic steady state was reached rapidly, CO2 slip in the product gas was reduced, and steam requirements were lowered.
In later experiments, it was demonstrated that the sorbent remained mechanically stable during operation of at least 2000 adsorption – desorption cycles, and that the CO conversion and CO2 slip remained constant as well. With this new, higher density material, carbon capture levels exceeding 95% can be obtained more efficiently and vessels will be smaller.
For testing of the cyclic SEWGS process in syngas from coal, refinery residues or blast furnaces, the test rig was adapted for operation using H2S containing gases. Breakthrough and cyclic tests were performed in order to investigate the effects of H2S on the sorbent capacity and stability. Observations confirm the earlier findings of small-scale studies that H2S did not influence the CO2 capacity significantly, and the H2S is cocaptured together with the CO2. A long-term test comprising 2000 cycles demonstrated that both the CO2 sorption capacity and the CO conversion were stable for the duration of the test. In total over 7000 cycles have been achieved.
In this task a reactor model was developed from first principles that can match the data collected from the single-column test rig at ECN. This model was first used to understand the natural gas based SEWGS system, and then extended to include other adsorbates in coal-based feeds. Experimental results from WP1 were used to provide an understanding on a number of sorbent materials of interest. These results were combined with heat and mass transfer parameters obtained from single-column breakthrough tests to enable a new physical model to be put together for the SEWGS process. The final model was compared against cyclic tests in the single-column test rig to verify and enhance its predictive capabilities. The model developed provided a basis for a tool created in WP3 in which more complex cycles were analysed.
By combining experimental data collected in WP1 and WP2. When present together in the gas phase, CO2 and stream were found to interact on the sorbent and affect the equilibrium capacity of each other. The experimental work carried out under CAEASR has allowed this factor to be evaluated and also be incorporated into the model.
There is a rapid change in the sorbent capacity for both CO2 and steam for low partial pressures (less than 1 bar), but this flattens out noticeably at higher partial pressures. From a cycle design perspective, the fact that the sorbent capacity for steam is essentially constant over a wide range of partial pressures is beneficial. This limits the amount of steam that is taken up or desorbed from the material over the course of a cycle and the dynamic capacity for steam effectively becomes zero. Unfortunately, in order to achieve a large cyclic capacity for CO2, the partial pressure in the gas phase must be decreased to a significantly low value to facilitate effective removal. This is achieved in the pressure-swing SEWGS process by reducing the total system pressure for regeneration and supplying purge gas (i.e. low-pressure steam) to further reduce the CO2 partial pressure and maximize the driving force for desorption.
Modelling of the ALKASORB Sorbent for the sorption-enhanced water-gas-shift (SEWGS) process
For the ALKASORB sorbent a model is created to simulate its performance. Breakthrough tests and cyclic experiments in both a single column and multi-column apparatus have been used for comparison. The model enables fast evaluation of the technology under different design scenarios and the results have been used to estimate performance on a commercial scale. Optimisation studies have been performed using the model to evaluate the behaviour of the SEWGS process under different designs and operating conditions. With the model matched reasonably well with the experimental data, the tool was used to predict the performance of commercial size units to allow an estimate of sizing and operating cost. This cycle varies from that practiced in the multi-column test rig simply in the introduction of pressure equalisation steps to reduce losses of H2 and pressure energy. Coupling of the model with full power plant sizing and costing shows that the optimised SEWGS process substantially lowers the cost of electricity when CO2 emissions must be minimised.
Alternative reactor set-ups
In CACHET, a number of different cycle designs were put together for a fixed bed sorption system. As an extension of this work, alternative sorption/reactor systems and alternative arrangements were evaluated in this task to see if these could bring additional benefits (cost savings) versus the fixed bed approach. Advantages and disadvantages of each were determined.
WP3 Advanced reactor design
The objectives of Work Package 3 are:
- Incorporation of the SEWGS cycles in the SEWGS simulations and experimental validation using the multi-column PDU.
- Using this model to develop a SEWGS process cycle with a total steam/CO2 ratio of 2 mole/mole.
- Experimental demonstration of the cycle on the multi-column test rig.
- Development and demonstration of the cyclic SEWGS process for application in coal gas and blast-furnace gas.
- Experimental results on SEWGS using the multi-column test rig
- Cyclic SEWGS process model validated with multi-column data
- SEWGS cyclic process model applied to a new sorbent
Adaptation of MC test rig
For testing of the cyclic SEWGS process in syngas from coal, refinery residues or blast furnaces, adaptation was necessary, including adaptations and addition of mass flow controllers in the feed section. Also, based on the CACHET testing, changes were necessary to improve the accuracy and reliability of the multi-column rig.
Multi-column troubleshooting tests
In the CACHET work, it was found that the results obtained for the SEWGS cycle in the multi-column rig seemed to be inconsistent with data collected in the single-column rig. The aim was to determine the differences between the single- and multi-column rigs and evaluate the impact of each on performance. Examples investigated include: bed length, flow rate, pressure, equalisation rate and other cycle steps. The tests led to an understanding as to what factors may have led to differences in performance so that these factors could be accounted for in the modelling. This work also led to a greater confidence in the accuracy of the data collected from the multi-column rig.
Multi-column experiments: new cycles and new applications
After having qualified the ALKASORB materials in the single-column, it was loaded in the multi-column rig. Gas compositions for multiple applications (natural gas, coal gas, blast furnace gas) were tested in the multi-column rig. The aim was to support the modelling work and show that SEWGS cycles can be developed that are economically viable. The tests also showed the effects of the most important operating conditions and the effects of feed composition under realistic conditions. The testing program comprised adsorption (breakthrough) tests, desorption tests, and cyclic tests. Breakthrough tests confirmed that the CO2 adsorption capacities observed in the multi-column rig were similar to the capacities observed in the single-column test rig. Desorption tests revealed the presence of kinetic limitations during purging. Knowledge of the desorption rates may help to optimise the sorbent regeneration strategy.
Cyclic tests demonstrated that the process reaches quasi-steady state operation in a few cycles, in contrary to the sorbent material tested in the CACHET project, where it could take a few hundred cycles before quasi-steady state operation was obtained. The ALKASORB sorbent is thus suited for performing tests and quality control. The tests showed that the CO2 stream purity was sensitive to the amount of rinse gas. The effect of the amount of rinse gas became noticeable in the H2 stream purity when a reactor was overrinsed: carbon would then slip through without improving the CO2 stream purity. The cyclic tests also showed that with the ALKASORB sorbent a steam-to-carbon ratio below 2 mole/mole is feasible, which is a reduction by 50% compared to the reference material. Tests with various syngas feeds show that the sorbent contained sufficient activity for the water-gas shift reaction that a separate water-gas shift catalyst was not required without substantial slip of CO in the H2 product gas. Furthermore, very pure H2 product gas could be obtained, at the expense of decreased cyclic capacity. Purities exceeding 99.99% were demonstrated, which may be relevant for gas purification applications of SEWGS, such as hydrogen production.
Multi-column SEWGS cycle modeling
Using the experience with conventional PSA units along with the fundamentals learnt from the single-column tests at high temperature, Air Products created an updated model for the SEWGS process. Experimental data from the multi-column rig was used to validate the model and enabled corrections to be made for those steps in the cycle that were not present in the single-column tests.
The composition of the syngas derived from a feedstock of natural gas or coal is notably different, and depends on the constituents of the fuel as well as the technology employed to produce the syngas. Within CAESAR, process design work on natural gas is based on an air-fired GHR-ATR combination (gas heated reformer-autothermal reformer). Similarly the performance of a SEWGS unit in an IGCC uses a Shell gasifier with bituminous coal. After reforming/gasification, the syngas is passed through a first water-gas-shift reactor. Whilst the SEWGS unit is capable of carrying out the water-gas-shift reaction, it is preferable to have the bulk of this work done in a separate unit as the resulting temperature increase due to the exothermic reaction negatively impacts the uptake of CO2 on the sorbent material. The composition of the syngas after the water-gas-shift reactor.
The compositions given are simplified to the major components in the feed used in the subsequent analysis. The most important difference between the two compositions is the substantially higher CO2 content of the coal derived syngas. This increases the challenge for the SEWGS process as the H2/CO2 ratio strongly affects the amount of sorbent material required.
There are a large number of parameters that can go into the design of a SEWGS process including feed conditions, regeneration pressure, steam rinse and purge flow rates, cycle time, vessel size, number of parallel trains. In the following analysis the cycle time, vessel size and number of trains were all kept constant.
The rinse and purge flow rates were then varied for different pressures, feed compositions and equalization steps to obtain a combined CO2 and CO capture rate of 95% with a CO2 -product purity of 95%.
In general, the modelling work shows that increasing the rinse gas flow rate results in an improved CO2 -product purity as it pushes more of the H2-rich gas out of the beds after the feed step. However, this also results in part of the adsorbed CO2 being removed from the vessel before the regeneration step and added back into the feed. Therefore, adding more rinse gas has the detrimental effect of increasing the sorption challenge for the SEWGS process, thereby decreasing the capture rate. The carbon capture rate can be improved by increasing the amount of purge steam used as this desorbs more CO2 from the sorbent, allowing more CO2 to be adsorbed during the feed step for the same cycle time. However, adding too much purge gas ultimately results in an decrease in CO2 purity given a fixed cycle time and vessel size. This is because increasing the adsorbent capacity decreases the average partial pressure of (CO2) inside the vessel at the end of the feed step. This allows more H2-rich gas to be present inside the vessel which must be removed by rinsing or otherwise it will contaminate the CO2 product. The overall result therefore is that the flows of rinse and purge gas must be balanced against each other to achieve the required carbon capture rate and CO2 purity.
Natural Gas Case
The amount of rinse steam required reduces by decreasing the feed pressure and/or increasing the number of equalization steps. A higher feed pressure results in a greater inventory of gas inside the vessel at the end of the feed step. Therefore more rinse gas is required to displace the residual H2 containing gas to reach the 95% CO2 purity specification. Adding equalization steps is also beneficial because not all the H2-rich gas must be displaced during the rinse step itself. Instead, during each equalization step residual H2-rich gas is removed and recaptured in a vessel being pressurized before the feed step. This reduces the amount of H2 and other contaminates left inside the vessel before regeneration. Using more equalization steps results in a marked reduction in the rinse gas requirement, without significantly increasing the purge gas amount. However, to incorporate an increased number of equalization steps into a cycle, more vessels are required and this therefore increases capital cost. It is found that the purge gas requirement generally increases as the feed pressure falls and/or more equalization steps are used. At the lowest feed pressures there is a large purge requirement because the maximum achievable capacity falls dramatically due to the reduced feed CO2 partial pressure.
As the maximum achievable CO2 capacity on feed drops, then the adsorbent must be more thoroughly regenerated during the purge step to maintain a similar dynamic capacity to the higher feed pressure cases. The increase in purge gas requirement with the number of equalization steps is mostly due to the fact that during each equalization step, the most easily removed CO2 is put into another vessel being pressurized. This not only reduces the amount of CO2 that can be removed during the subsequent regeneration step (i.e. the driving force for CO2 removal goes down) but also preloads a regenerated bed with CO2 so that it has less capacity available for the feed step. Therefore more purge gas is required to counteract these effects and achieve the same dynamic capacity.
The amounts of rinse and purge steam are not absolute requirements and can be changed by modifying the vessel size, cycle time and/or cycle arrangement. The value placed on the high pressure steam used for rinsing is obviously greater than the low pressure steam used for purging, so it is only through a full process optimization that the actual amounts of each to be used can be determined. However, the results indicate that the optimum design for a SEWGS unit is probably towards the middle of this pressure range, 20-30 bara. Operating at higher pressures results in a substantial increase in rinse gas requirement for no improvement in overall performance, whilst at lower pressures the purge gas requirement increases markedly. Fortunately, this pressure range matches well with feeding directly into a gas turbine. For the conditions used in this particular analysis, the 20-30 bara range with 3 equalization steps gives required rinse steam to feed carbon ratios of 0.65-1.00 and similar 1.55-1.15 for purge steam (i.e. a total steam to feed carbon ratio of 2.15-2.20 versus a goal of 2.0).
In the same manner as for natural gas, an analysis on steam purge and rinse flow rates was carried out with a coal-derived syngas feed. The only difference between the two cases in terms of input was that the adsorbent volume was doubled to accommodate the greater CO2 challenge for the same cycle time. The capacity of the sorbent does not increase linearly with the partial pressure of CO2 in the feed, and is almost flat at high partial pressures. Therefore the amount of adsorbent required to remove the CO2 in the feed gas must be increased roughly in proportion to that in the syngas.
For all conditions more rinse gas per unit of feed gas is required for the coal case because the amount of sorbent was increased, which leads to more H2-rich gas being present inside the vessel after the feed step. However, the rinse gas required does not double in-line with the increase in adsorbent as the higher CO2 and steam partial pressures in the feed syngas reduce the residual quantity of H2 inside the vessel. The purge gas requirement follows some of the same trends as for the natural gas case, with the flow rate increasing at the lower end of the feed pressure range. However, for one and even two equalization steps, there is also an increase in purge gas requirement at the upper end of the feed pressure range. The upturn in purge gas flow rate coincides with the rinse gas flow rate increasing above 40% of the feed flow. As with the natural gas case and the optimum feed pressure range appears to be 20-30 bara. This leads to a ratio of steam rinse to carbon in the feed of 0.40-0.65 and similarly a purge steam requirement of 1.50-1.25 (a total steam to carbon ratio of 1.90). Compared with natural gas, this gives a lower steam to carbon ratio, primarily due to a reduction in the requirement of rinse steam to feed carbon. However, the size or number of vessel used for the coal case must be doubled to achieve these results. This is a notable increase in capital cost that must be factored into the economic analysis for using SEWGS with a coal based feed.
The model was used in Work package 4 to develop the most efficient fixed bed cycles for SEWGS in various applications (natural gas, coal, etc.).
WP4 Application and process integration
Development of flow sheet models and costing tools for the new SEWGS set-up for natural gas fired power generation and for coal gas and industrial applications (refinery residues gasification and blast-furnace gas). SEWGS system with an efficiency penalty of less than 5% point and capture costs of 15EUROS/ton CO2 compared to the CACHET base case i.e. NGCC with ATR-WGS-CO2 separation and compression or an IGCC with WGS and separation and compression.
- European bench marking task force (EBTF) and bench mark common frame work definition document to be used in the three EU PF7 RTD projects on capture technology development i.e CESAR, CAESAR and DECARBit;
- Development (in the framework of the EBTF task force activities) of the reference base case for the SEWGS application in a natural gas combined cycle (NGCC) power plant, in an integrated gasification combined cycle (IGCC) power plant and finally in a blast furnace gas combined cycle power plant
- Techno economic assessments of the SEWGS capture process in NGCC, in IGCC and BFCC including several peer reviewed publications
European bench mark taskforce (EBTF) and reference base case
The EBTF is team of participants of three CCS Research and Development (R&D) projects, which are DECARBit, CAESAR and CESAR. In their framework document the EBTF defines a set of parameters to be applied to the study of CCS technologies in these three projects and in future European CCS Research and Development (R&D) projects. Such parameters are related to ambient conditions, fuels, gas separation, coal gasification, shift reaction, gas turbine, steam cycle, heat exchangers, efficiency calculations, emission limits and economic assessment criteria. Its purpose is to serve as a basis for cycle definition, cycle analysis, comparison of different technologies and comparison of economic evaluations, making such comparisons consistent and reliable, by being based on the same set of fundamental assumptions. It builds on previous work carried out in FP6 projects, in particular ENCAP, DYNAMIS, CASTOR and CACHET.
The report begins with the very basic selection of unit system and ambient conditions. It then describes the characteristics of three types of fuel: Bituminous coal, lignite and natural gas. As the objective of the projects of interest is to study the technologies of power generation, the authors think that three standard compositions are sufficient. After these definitions, the report describes the choice of parameters for a number of modules or processes of the power plants objective of study. Such modules and processes are air separation, coal gasification, shift reaction, gas turbine, steam cycle and heat exchangers. Then more general issues are defined: the procedure for efficiency calculation, CO2 treatment and emission limits from solid fuels. Finally, criteria for economic assessments of new technologies and cycles are established.
Within the framework of the EBTF the reference base cases for the SEWGS technology were defined. Fort the NGCC the reference base case is the post combustion capture, whereas the reference base case for IGCC is pre combustion with SELEXOL. These two reference case were defined and approved by the industrial partners in the EBTF (Shell, Alstom, E-ON and Shell).
Techno economic assessments of the SEWGS capture process in NGCC, in IGCC and BFCC
The techno economic assessment for the SEWGS application in NGCC and IGCC are based on the results of the extensive ALKASORB testing in both the single column and multi column test rig and the SEWGS cycle optimisation and cost estimates. In the final year work to improve the capacity of AKASORB sorbent continued and resulted in a improved sorbent (ALKASORB+) with a substantial higher capacity. Therefore, the techno – economic assessments for the SEWGS application both natural gas and coal fuelled power plants have been up-dated in the final month of the project.
SEWGS application in NGCC
The cost of electricity (COE) for NGCC without CO2 capture is 54.10 EUROS/MWh. The COE depends on fuel costs (as typical of NG based power plants), while the sum of fixed and variable costs accounts for less than 10%. In the CO2 capture case, COE increases 15-20 EUROS/MWh as consequence of the higher investment costs and lower efficiency which leads to higher specific fuel consumption. The calculated cost of CO2 avoided for MEA and MDEA cases are 47.5 EUROS/t CO2 and 63.8 EUROS/t CO2.
The cost of electricity (COE) for NGCC without CO2 capture is 54.10 EUROS/MWh. The COE depends on fuel costs (as typical of NG based power plants), while the sum of fixed and variable costs accounts for less than 10%. In the CO2 capture case, COE increases 15-20 EUROS/MWh as consequence of the higher investment costs and lower efficiency which leads to higher specific fuel consumption. The calculated cost of CO2 avoided for MEA and MDEA cases are 47.5 EUROS/t CO2 and 63.8 EUROS/t CO2. The cost of CO2 avoided for the MEA case is lower compared to similar studies in the literature, however it can represent advanced solution amine scrubbing.
For the SEWGS cases, the number of SEWGS vessels and the vessel heights were optimised with respect to lowest levelised costs. SEWGS with ALKASORB has a cost of CO2 avoided lower than reference pre-combustion technology (58.6 EUROS/t CO2 vs. 63.8 EUROS/t CO2), but 9 EUROS/t CO2 higher compared to post-combustion technology. This is because the higher electric efficiency and CO2 avoided rate of SEWGS does not compensate the additional costs of pre-combustion lay-out; in addition to the SEWGS unit also a reformer section is necessary negatively affecting specific investment costs.
The use of the improved ALKASORB+ sorbent reduces the cost of CO2 avoided to 49 EUROS/t CO2 which close to the post combustion MEA case. Results showed that for the SEWGS cases, CO2 purity has a negligible impact from a economic point of view, thus higher CO2 purity is preferred to reduce transport and storage issues related to the CO2 quality. Since ALKASORB+ requires much less steam, the specific energy consumption (SPECCA) is substantially reduced to 25% below the specific energy consumption for the MEA post combustion technology (2.53 versus 3.36 MJLHV/kg CO2).
SEWGS application in IGCC
The COE for the reference case IGCC is about 66 EUROS/MWh. More than 50% of the COE depends on the investment costs, while fuel costs account for about 35%. This result is typical for coal based plants, while natural gas based plants have an opposite trend. COE for the CO2 capture cases increases 35% because of the higher investment cost as well as higher fuel costs. The resulting cost of CO2 avoided is 36.5 EUROS/t CO2 which is in the range of similar studies proposed in literature supporting the reliability of this analysis.
The cost of electricity for reference IGCC is about 66 EUROS/MWh. More than 50% of the COE depends on the investment costs, while fuel costs account for about 35%. This result is typical for coal based plants, while natural gas based plants have an opposite trend. COE for the CO2 capture cases increases 35% because of the higher investment cost as well as higher fuel costs. The resulting cost of CO2 avoided is 36.5 EUROS/t CO2 which is in the range of similar studies proposed in literature supporting the reliability of this analysis.
The application of SEWGS ALKASORB in an IGCC allows reducing the cost of electricity to about 86 EUROS/MWh i.e. 2.5% less than in the SELEXOL case. The avoidance rate of SEWGS ALKASORB is however, over 6% points higher. SEWGS reduces investment and also the fuel costs due to the co - capture of sulphur and consequent equipment costs savings, and higher efficiency. Only consumables, which mainly depend on sorbent replacement, are higher. With the new ALKASORB+ sorbent the COE is reduced to 81,5 EUROS/MWh. Accordingly, the cost of CO2 avoided is reduced to approx. 23 EUROS/t CO2 which is a reduction of more than 30% compared to the SELEXOL capture case.
Application of SEWGS in blast furnace fuelled combined cycles
Next to the NGCC and IGCC application the application of SEWGS for in a blast furnace combined cycle was assessed. The first step consisted of developing reference cases for this application and it is based on EBTF common framework definition document. Considering that blast furnace gas has a low heating value (both from volumetric and mass flow point of view), a dedicated gas turbine design was taken into account and no significant penalties for this application have been applied. The resulting efficiency is 52.4% with specific emissions of 1.3 kg CO2 /kWh, that's about twice coal plant and four times NGCC applications.
Next, a reference case with CO2 post combustion capture was performed: CO2 capture was based on amine technology with ancillaries consumption specifically calculated (the higher CO2 content in the exhaust gas slightly reduces the specific heat duty for MEA regeneration). Because of the large CO2 mass flow compared to the heating value, the steam produced in the HRSG is enough only to capture part of the CO2 even with the adoption of a back pressure turbine plant. Efficiency penalties are in the range of 18 -20% depending on natural gas addition. Performances of cases investigated show that SEWGS reduces Specific Energy Consumptions for CO2 avoided (SPECCA) with about 70% compared to reference MEA case due to the higher CO2 avoided rate.
WP5 Process scale-up
The objectives of Work Package 5 are:
- Make a choice, based on the outcome of WP 4, for what application the design will be made.
- Understand the key technical risks of this technology at full scale deploy, and develop the objectives of a pilot plant program that will provide full mitigation.
- Deliver the critical aspects of a Process Design Package for a pilot plant for one of the applications studied, with specific focus on the vessel design and switching valves.
In this WP5 the requirements and objectives of a pilot plant were defined. This information was used as basis to evaluate a number of potential host sites for the pilot unit. Previous work had highlighted that critical design work was needed to include the mechanical design of the vessel and to ensure availability of suitable high temperature, high differential pressure valves which are able to operate reliably with good isolation characteristics over multiple cycles.
Since a suitable site could not be selected in time (originally planned at the last quarter of 2010), site-specific issues could not be taken into the design. Hence, a more general design approach was taken, enabling the work to remain valid should the site selection be re-evaluated at a later date. The generic design issues addressed included the design and costing of the reactor vessels, valve availability, and a general HSE review.
- Pilot plant scope of requirements and objectives
- Optimised flow sheet with configuration of vessels and switch valves
- Mechanical reactor design for pilot plant
- High temperature valve availability from suppliers
- Learning's from the design, construction and operation of a multi-column unit.
The SEWGS process has distinct characteristics for separating CO2 and hydrogen, giving the potential to improve the efficiency and lower the cost of CO2 capture. The relative merits of these characteristics will affect the value of the integration of the process compared with the state of the art. Analysis of the SEWGS characteristics suggested that the application to combined cycle power production (NGCC, IGCC and BF-CC) remains the most likely application for the SEWGS technology. Other applications investigated appeared to be less obvious with likely lower economic benefits.
Requirements and objectives
On basis of the conclusion that the highest economic benefits for the SEWGS pre-combustion capture technology in the power generation is either a natural gas fuelled combined cycle combined cycle (NGCC), a coal gas fuelled combined cycle (IGCC) or a blast furnace gas combined cycle (BFCC), the scope of requirements and objectives for a SEWGS pilot plant were established.
The SEWGS technology was evaluated using NASA's technology readiness level methodology. By the end of 2010, the SEWGS process was classified on level 5 – 6. At the end of the CAESAR project (December 2011) SEWGS development was ready to move to the next development level, which is a pilot plant installation of which the capacity is on the order of 100 times larger than the current multi-column Process Development Unit, but still on the order of 100 times smaller than a commercial scale installation. This pilot plant must use real fuel gas to demonstrate long term stability of the ALKASORB sorbent.
The primary objectives of a pilot plant are:
- Prove SEWGS performance on sufficient scale and under field conditions
- Confirm scale-up parameters and assurance of modelling results
- Prove the design is fit for purpose
- Optimise the cycle design
The main requirements of a pilot unit include availability of syngas, power, steam, nitrogen, cooling fluid, instrument air, process water, waste disposal of condensate, CO2 and H2.
Furthermore, an inventory of critical items for the SEWGS technology was made. These issues will need to be addressed in the pilot project.
In the course of 2011, a suitable host site was identified, and a SEWGS pilot validation project proposal was made. The pilot project was scheduled for the period 2012 – 2016. The consortium comprised European companies, a research organisation and a university.
Optimised configuration and plant reliability
The optimised cycle and configuration were established, the impact of possible switch valve leakage on the SEWGS process was studied, and ways to minimise the impact through cost effective measures were identified. The impact of the reliability of the switch valves on the overall availability of the SEWGS process was studied and recommendations were made to improve reliability whenever this would be required from an operability standpoint. Moreover, strategies were proposed and compared in order to allow valve maintenance without shutting down the plant.
Vessel design and availability of high-temperature valves
For the mechanical design of the vessels, the frequent pressure swings are of critical importance for the fatigue analysis. Several design alternatives were proposed and assessed, taking into account the applicable codes and standards, and the best design was selected. Cost estimations for this vessel were obtained.
Specifications for the high-temperature valves were made, using the optimised configuration of vessels and valves established earlier in the project. The availability and prices of the valves were obtained from vendors. Various suitable valves were identified, and valve availability did not appear to be an issue, although delivery times could be substantial. Using the latest cost estimates for vessels and high-temperature valves, it appeared that the updated cost estimate for a SEWGS unit was not in line with prior preliminary cost estimates of a SEWGS unit (cost estimates were corrected for inflation towards the same base year).
WP6 Project management and dissemination
The objectives of Work Package 6 are:
- Dissemination of the project results
- Organisation of a yearly EU CCS Conference
Dissemination of project results
In total 11 peer reviewed papers will be published in scientific journals. 8 papers have already been published, another 3 are in the reviewing stage and will be published in 2012. Finally, the consortium has submitted one abstracts for the GHGT11 conference in Kyoto presenting an overview of the headline results of CAESAR and another one on the sorbent (ALKASORB) development in CAESAR. Finally, a publication is in preparation on the SEWGS modelling activities.
The CAESAR consortium performed several dissemination activities including presentations on the CARBON DIOXIDE (CO2) net meetings in 2008, 2009, 2010 and 2011, presentations during the Trondheim CCS in 2009 and 2011 conferences. Furthermore the consortium presented the CAESAR project results during the GHGT-10 conference in Amsterdam and during the Pittsburgh CCS conference in 2009 and 2011. Other dissemination activities concern flyers, posters and a video on the SEWGS technology. This video is available on the CAESAR website: http://CAESAR.ecn.nl/home/
Organisation of a yearly EU CCS Conference
The three Seventh Framework Programme (FP7) projects on CO2 capture will organise for the next three years an annual EU CCS conference. A rotating Chairman organisation –and expenses- has been jointly established with DECARBit and CESAR for three years (2009, 2010 and 2011), inviting new FP7 project to join in during the these years. The CAESAR consortium assisted the coordinators of DECARBit and CESAR in organising of the first two meetings in Oslo (2009) and Rotterdam (2010) and organised the 3rd EU CCS conference in London, (24 – 26 of May) in cooperation with CO2 net. Almost all ongoing European projects on CCS (including those in supported by RFCS presented their latest results. As such the conference was a success in establishing a forum for dissemination of project result as well as for sharing information between EU funded projects on CCS. The 160 participant evaluated the this EU CCS conference very positive and suggested that the series will be continued in the coming years. The coordinators of the first three FP7 projects (CESAR, CAESAR and DECARBit) and CO2 net therefore invite the commission to discuss how to continue this conference series during remainder of the FP7 programme.
To maintain European economic competitiveness, it will be vital to reduce the cost of capturing greenhouse gas emissions from European power generation plants, refining and other energy intensive industrial processes, while reducing the cost of H2 production as Europe moves towards a H2 economy. The CAESAR project resulted CO2 avoided cost of about 23 EUROS/t CO2 for pre combustion CO2 capture with the SEWGS integrated in an IGCC power plant. This avoided cost can be translated to capture cost of about 17 EUROS/t CO2 which is almost the target value of 15 EUROs. The low capture cost is the result of several improvements in the SEWGS technology i.e. a reduction in the steam consumption in the rinse and purge step, a new sorbent with a almost 100% higher CO2 capacity and finally improved integration of the SEWGS technology in the power plant cycle optimisation on basis of a special developed SEWGS model which uses measured isotherms. Although the IGCC application is the most favourable application for the SEWG capture process, the improvements also resulted in a reduction of almost 50% (100 to 50 EUROS/t CO2 of the capture cost for the natural gas combined cycle application. The low capture cost could certainly speed up the implementation of CCS in power generation and makes the CCS technology even more competitive with other low carbon technologies.
The SEWGS technology is evaluated using NASA's technology readiness level (TRL) methodology. By the end of 2010, the SEWGS process was classified on level 5 – 6, of the max 9 TRL levels. At the end of the CAESAR SEWGS development was ready to move to the next development level, which is a pilot plant installation of which the capacity is on the order of 200 times larger than the current multi-column unit, but still on the order of 100 times smaller than a commercial scale installation. This pilot plant will use real fuel gas to demonstrate long term stability of the new sorbent.
However, with the current CO2 prices levels in the ETS, there is currently no business case or CCS in power generation which makes the of the next phase in the SEWGS development very difficult. Other interesting application of the SEWGS technology is the decarbonisation of blast furnace gas and other industrial applications. The SEWGS technology has been identified as platform technology also to be used in other non CCS application like conventional hydrogen production, ammonia production and refinery residue gasification.
Overview of markets and their respective sizes
The blast furnace gas market can be a retrofit market, and although not many steelworks currently use the blast furnace gas in a gas turbine combined, the amount of SEWGS units required by a single steelwork is significant. Also, it is expect this market will grow quickly in the upcoming years. The market for IGCC is also a retrofit market. The amount of installations required for IGCC is quite a bit lower than for blast furnace gas. The NGCC and ammonia market are not suitable for retrofit, so the growth of the market demand is primarily required from the newly installed plants and thus restricting the number of SEWGS units. The cost savings for an IGCC power plant of 400 MWe are in the other of 20 M EUROS per year compared to the conventional process i.e. Selexol. Also in the blast furnace application considerable cost savings are possible compared to the current MEA post combustion capture technology.
Dissemination of project results
In total 11 peer reviewed papers will be published in scientific journals. 8 papers have already been published, another 3 are in the reviewing stage and will be published in 2012. Finally, the consortium has submitted abstracts for the GHGT11 conference in Kyoto presenting an overview of the headline results of CAESAR (one abstract) and another one on the sorbent (ALKASORB) development in CAESAR. Finally, a publication is in preparation on the SEWGS modelling activities.
The CAESAR consortium performed several dissemination activities including presentations on the CO2 net meetings in 2008, 2009, 2010 and 2011, presentations during the Trondheim CCS in 2009 and 2011 conferences. Furthermore the consortium presented the CAESAR project results during the GHGT-10 conference in Amsterdam and during the Pittsburgh CCS conference in 2009 and 2011. Other dissemination activities concern flyers, posters and a video on the SEWGS technology. This video is available on the CAESAR website: http://CAESAR.ecn.nl/home/
Organisation of a yearly EU CCS Conference
The three FP7 projects on CO2 capture will organise for the next three years an annual EU CCS conference. A rotating Chairman organisation –and expenses- has been jointly established with DECARBit and CESAR for three years (2009, 2010 and 2011), inviting new FP7 project to join in during the these years. The CAESAR consortium assisted the coordinators of DECARBit and CESAR in organising of the first two meetings in Oslo (2009) and Rotterdam (2010). The CAESAR consortium organised the 3rd EU CCS conference in London, (24 – 26 of May) in cooperation with CO2 net. Almost all ongoing European projects on CCS (including those in supported by RFCS presented their latest results. As such the conference was a success in establishing a forum for dissemination of project result as well as for sharing information between EU funded projects on CCS. The 160 participant evaluated the this EU CCS conference very positive and suggested that the series will be continued in the coming years. The coordinators of the first three FP7 projects (CESAR, CAESAR and DECARBit) and CO2 net therefore invite the commission to discuss how to continue this conference series during remainder of the FP7 programme.
List of websites:
Grant agreement ID: 213206
1 January 2008
31 December 2011
€ 3 143 422
€ 2 263 515
STICHTING ENERGIEONDERZOEK CENTRUM NEDERLAND
This project is featured in...
Deliverables not available
Grant agreement ID: 213206
1 January 2008
31 December 2011
€ 3 143 422
€ 2 263 515
STICHTING ENERGIEONDERZOEK CENTRUM NEDERLAND
This project is featured in...
Grant agreement ID: 213206
1 January 2008
31 December 2011
€ 3 143 422
€ 2 263 515
STICHTING ENERGIEONDERZOEK CENTRUM NEDERLAND