Liang-Shih
FAN
Coal-Direct Chemical Looping
http://hardware.slashdot.org/story/13/02/21/2336200/new-process-takes-energy-from-coal-without-burning-it
New
Process Takes Energy From Coal Without Burning It
"Ohio State students
have come up with a scaled-down version of a power plant
combustion system with a unique experimental design--one that
chemically converts coal to heat while capturing 99 percent of
the carbon dioxide produced in the reaction. Typical coal-fired
power plants burn coal to heat water to make steam, which turns
the turbines that produce electricity. In chemical looping, the
coal isn't burned with fire, but instead chemically combusted in
a sealed chamber so that it doesn't pollute the air. This new
technology, called coal-direct chemical looping, was pioneered
by Liang-Shih Fan, professor of chemical and biomolecular
engineering and director of Ohio State's Clean Coal Research
Laboratory."
http://researchnews.osu.edu/archive/looping203.htm
Ohio State University Research and Innovation
Communications
New
Coal Technology Harnesses Energy Without Burning, Nears
Pilot-Scale Development
by Pam Gorder
COLUMBUS, Ohio—A new form of clean coal technology reached an
important milestone recently, with the successful operation of a
research-scale combustion system at Ohio State University. The
technology is now ready for testing at a larger scale.
For 203 continuous hours, the Ohio State combustion unit
produced heat from coal while capturing 99 percent of the carbon
dioxide produced in the reaction.
Liang-Shih Fan, professor of chemical and biomolecular
engineering and director of Ohio State’s Clean Coal Research
Laboratory, pioneered the technology called Coal-Direct Chemical
Looping (CDCL), which chemically harnesses coal’s energy and
efficiently contains the carbon dioxide produced before it can
be released into the atmosphere.
“In the simplest sense, combustion is a chemical reaction that
consumes oxygen and produces heat,” Fan said. “Unfortunately, it
also produces carbon dioxide, which is difficult to capture and
bad for the environment. So we found a way to release the heat
without burning. We carefully control the chemical reaction so
that the coal never burns—it is consumed chemically, and the
carbon dioxide is entirely contained inside the reactor.”
Dawei Wang, a research associate and one of the group's team
leaders, described the technology’s potential benefits. "The
commercial-scale CDCL plant could really promote our energy
independence. Not only can we use America's natural resources
such as Ohio coal, but we can keep our air clean and spur the
economy with jobs," he said.
“We carefully control the chemical reaction so that the coal
never burns—it is consumed chemically, and the carbon dioxide is
entirely contained inside the reactor.”
Though other laboratories around the world are trying to develop
similar technology to directly convert coal to electricity,
Fan’s lab is unique in the way it processes fossil fuels. The
Ohio State group typically studies coal in the two forms that
are already commonly available to the power industry: crushed
coal “feedstock,” and coal-derived syngas.
The latter fuel has been successfully studied in a second
sub-pilot research-scale unit, through a similar process called
Syngas Chemical Looping (SCL). Both units are located in a
building on Ohio State’s Columbus campus, and each is contained
in a 25-foot-high insulated metal cylinder that resembles a very
tall home water heater tank.
No other lab has continuously operated a coal-direct chemical
looping unit as long as the Ohio State lab did last September.
But as doctoral student Elena Chung explained, the experiment
could have continued.
“We voluntarily chose to stop the unit. We actually could have
run longer, but honestly, it was a mutual decision by Dr. Fan
and the students. It was a long and tiring week where we all
shared shifts,” she said.
Fan agreed that the nine-day experiment was a success. “In the
two years we’ve been running the sub-pilot plants, our CDCL and
SCL units have achieved a combined 830 operating hours, which
clearly demonstrates the reliability and operability of our
design,” he said.
At any one time, the units each produce about 25 thermal
kilowatts—that is, thermal energy, which in a full-scale power
plant would be used to heat water and turn the steam-powered
turbines that create electricity.
The researchers are about to take their technology to the next
level: a larger-scale pilot plant is under construction at the
U.S. Department of Energy’s National Carbon Capture Center in
Wilsonville, AL. Set to begin operations in late 2013, that
plant will produce 250 thermal kilowatts using syngas.
The key to the technology is the use of tiny metal beads to
carry oxygen to the fuel to spur the chemical reaction. For
CDCL, the fuel is coal that’s been ground into a powder, and the
metal beads are made of iron oxide composites. The coal
particles are about 100 micrometers across—about the diameter of
a human hair—and the iron beads are larger, about 1.5-2
millimeters across. Chung likened the two different sizes to
talcum powder and ice cream sprinkles, though the mix is not
nearly so colorful.
The coal and iron oxide are heated to high temperatures, where
the materials react with each other. Carbon from the coal binds
with the oxygen from the iron oxide and creates carbon dioxide,
which rises into a chamber where it is captured. Hot iron and
coal ash are left behind. Because the iron beads are so much
bigger than the coal ash, they are easily separated out of the
ash, and delivered to a chamber where the heat energy would
normally be harnessed for electricity. The coal ash is removed
from the system.
The carbon dioxide is separated and can be recycled or
sequestered for storage. The iron beads are exposed to air
inside the reactor, so that they become re-oxidized be
used again. The beads can be re-used almost indefinitely, or
recycled.
Since the process captures nearly all the carbon dioxide, it
exceeds the goals that DOE has set for developing clean energy.
New technologies that use fossil fuels should not raise the cost
of electricity more than 35 percent, while still capturing more
than 90 percent of the resulting carbon dioxide. Based on the
current tests with the research-scale plants, Fan and his team
believe that they can meet or exceed that requirement.
The DOE funded this research, and collaborating companies
include Babcock & Wilcox Power Generation Group, Inc.;
CONSOL Energy, Inc.; and Clear Skies Consulting, LLC.
Contacts: L.-S. Fan, (614) 688-3262; Fan.1@osu.edu
Elena Chung, (614) 247-2787; Chung.461@osu.edu
Liang-Shih
Fan
SYSTEMS
AND METHODS OF CONVERTING FUEL
WO2007082089
[ PDF ]
[0002] The present
invention is generally directed to systems and methods of
converting fuel, and is generally directed to
oxidation-reduction reactor systems used in fuel conversion.
[0003] There is a constant need for clean and efficient energy
generation systems. Most of the commercial processes that
generate energy carriers such as steam, hydrogen, synthesis gas
(syngas), liquid fuels and/or electricity are based on fossil
fuels. Furthermore, the dependence on fossil fuels is expected
to continue in the foreseeable future due to the much lower
costs compared to renewable sources. Currently, the conversion
of carbonaceous fuels such as coal, natural gas, petroleum coke
is usually conducted through a combustion or reforming process.
However, combustion of carbonaceous fuels, especially coal, is a
carbon intensive process that emits large quantities of carbon
dioxide to the environment. Sulfur and nitrogen compounds are
also generated in this process due to the complex content in
coal.
[0004] Chemical reactions between metal oxides and carbonaceous
fuels, on the other hand, may provide a better way to recover
the energy stored in the fuels. Several processes are based on
the reaction of metal oxide particles with carbonaceous fuels to
produce useful energy carriers. For example, Ishida et al. U.S.
Pat. No. 5,447,024 describes processes wherein nickel oxide
particles are used to convert natural gas through a chemical
looping process into heat, which may be used in a turbine.
However, recyclability of pure metal oxides is poor and
constitutes an impediment for its use in commercial and
industrial processes. Moreover, this technology has limited
applicability, because it can only convert natural gas, which is
more costly than other fossil fuels. Another well known process
is a steam-iron process, wherein coal derived producer gas is
reacted with iron oxide parlicles in a fiuidized bed reactor to
be later regenerated with steam to produce hydrogen gas. This
process however suffers from poor gas conversion -0-
[0005] rates due to improper contact between reacting solids and
gases, and is incapable of producing a hydrogen rich stream.
[0006] As demands increase for cleaner and more efficient
systems of converting fuel, the need arises for improved
systems, and system components therein, which will convert fuel
effectively, while reducing pollutants.
[0007] In one embodiment of the present invention, a system for
converting fuel is provided. The system comprises a first
reactor comprising a plurality of ceramic composite particles,
wherein the ceramic composite particles comprise at least one
metal oxide disposed on a support. The first reactor is
configured to reduce at least one metal oxide with a fuel to
produce a reduced metal or a reduced metal oxide. The system
also comprises a second reactor configured to oxidize the
reduced metal or reduced metal oxide to produce a metal oxide
intermediate, and a third reactor configured to regenerate at
least one metal oxide by oxidizing the metal oxide intermediate.
[0008] In another embodiment of the present invention, a method
of converting fuel to hydrogen, CO, or syngas is provided. The
method comprises the steps of: reducing a metal oxide in a
reduction reaction between a fuel and a metal oxide to a reduced
metal or a reduced metal oxide; oxidizing the reduced metal or
reduced metal oxide with an oxidant to a metal oxide
intermediate, while also producing hydrogen, CO, or syngas; and
regenerating the at least one metal oxide by oxidizing the metal
oxide intermediate.
[0009] In yet another embodiment, a system comprising a
Fischer-Tropsch reactor is provided. The Fischer-Tropsch reactor
is configured to produce hydrocarbon fuel from a feed mixture
comprising gaseous fuel. The system also comprises a first
reactor comprising a plurality of ceramic composite particles,
wherein the ceramic composite particles comprise at least one
metal oxide disposed on a support. The first reactor is
configured to reduce the metal oxides with a gaseous fuel to a
reduced metal or a reduced metal oxide, wherein the gaseous fuel
comprises at least partially the hydrocarbon fuel produced by
the Fischer-Tropsch reactor. The system also comprises a second
reactor configured to oxidize the reduced metal or reduced metal
oxide with steam to produce metal oxide intermediates.
[0010] In another embodiment, a method of preparing ceramic
composite particles is provided. The method comprises reacting a
metal oxide with a support material; heat treating the mixture
of metal oxide and support material at temperatures of between
about 200 to about 1500 <0>C to produce ceramic composite
powders; converting the ceramic composite powders into ceramic
composite particles; and reducing and oxidizing the ceramic
composite particles prior to use in a reactor...
HIGH
PURITY, HIGH PRESSURE HYDROGEN PRODUCTION WITH IN-SITU CO2
AND SULFUR CAPTURE IN A SINGLE STAGE REACTOR
US7837975
[ PDF ]
BACKGROUND
AND SUMMARY OF THE INVENTION
[0003] The disclosed embodiments includes a process for
producing hydrogen, comprising the steps of: (a) gasifying a
fuel into a raw synthesis gas comprising CO, hydrogen, steam and
sulfur and halide contaminants in the form of H2S, COS and HX,
where X is a halide; (b) passing the raw synthesis gas through a
water gas shift reactor (WGSR) into which CaO and steam are
injected, the CaO reacting with the shifted gas to remove CO2,
sulfur and halides in a solid-phase calcium-containing product
comprising CaCO3, CaS and CaX2; (c) separating the solid-phase
calcium-containing product from an enriched gaseous hydrogen
product; and (d) regenerating the CaO by calcining the
solid-phase calcium-containing product at a condition selected
from the group consisting of: in the presence of steam, in the
presence of CO2, in the presence of synthesis gas, in the
presence of H2 and O2, under partial vacuum, and combinations
thereof.
[0004] The fuel could be coal, biomass, oil sands, coke, tar,
wax oil shales, or combinations of these materials.
[0005] Although the steam may be injected into the WGSR in any
functional quantity, it is preferred that the steam injected is
in the range of from about the stoichiometric requirement to
about 3 times the stoichiometric requirement.
[0006] In one embodiment, the enriched hydrogen product has a
purity of at least 60%. In one embodiment, the H2:CO ratio of
the enriched hydrogen product is in the range of from about
0.5:1 to about 1000:1. In some embodiments the enriched hydrogen
product has a purity in the range of from about 70% to about
99.99%, at temperature in the range of from about 400-1000 C,
and a pressure in the range of from about 1 to about 100
atmospheres.
[0007] The WGSR may be of a type selected from the group
consisting of: fixed bed reactors, fluidized bed reactors,
entrained flow reactors, moving bed reactors rotary kilns, or
combinations thereof. Additionally, the calcinations step may be
performed in a calcinations reactor of a type selected from the
group consisting of: fixed bed reactors, fluidized bed reactors,
entrained flow reactors, moving bed reactors rotary kilns, or
combinations thereof.
[0008] In some embodiments, the WGSR does not have a catalyst
disposed therein. As such the WGSR operates at a temperature in
the range of from about 550-750 C, in the pressure range of from
about 1 to about 60 atm, it is preferred that the WGSR reactor
operate in a temperature range of from about 600-700 C and at a
pressure in the range of from about 20 to about 30 atm. In some
embodiments, the enriched hydrogen product is 99% pure when 3
times the stoichiometric steam requirement is used. At the
stoichiometric steam requirement the process produces an
enriched hydrogen product that is 90% pure. In another catalytic
embodiment, the enriched hydrogen product has a H2/Co ration of
at least 2.5 and a maximum sulfur (H2S/COS) concentration of
less than 10 ppm using only the stoichiometric requirement of
steam.
[0009] In some embodiments, a catalyst may be used in the WGSR.
A suitable high temperature shift catalyst which may include:
Fe, Cu, Co, Mo, W, Cs, Pt, Ph, Pd, and other precious metal
catalysts or their oxides or sulfides or combinations thereof.
Suitable supports for use with the foregoing high temperature
shift catalysts include: Cr2O3, ZnO, MgO, ceria, alumina,
silica, zirconia and combinations thereof.
[0000] A WGSR reactor with a catalyst operates in the
temperature range of from about 550-750 C and at a pressure in
the range of from about 1 to about 100 atm. It is preferred that
the WGSR reactor operate in the temperature range of from about
600-700 C and at a pressure of from about 20 to about 30 amt.
When a catalyst is used the enriched hydrogen product may
achieve 99.99% purity when 3* the stoichiometric requirement of
steam is used in the WGSR. The enriched hydrogen product may
achieve 98% purity when the stoichiometric requirement of steam
is used. Some embodiments may attain a purity of at least 80%
with a maximum sulfur (H2S/COS) concentration of less than 10
ppm when 3* the stoichiometric requirement of steam is used and
at least 70% purity with a maximum sulfur concentration of less
than 1 ppm when the stoichiometric requirement of steam is used.
[0010] The process may also comprise the step of (e) recycling
at least a portion of a product stream from a Fischer-Tropsch
reactor, fed by the WGSR, so as to introduce a chemical species
selected from the group consisting of: methane, C1-C4
hydrocarbons, CO, hydrogen and combinations thereof back into
the WGSR.
[0011] In all embodiments, the CaO may have a surface area of at
least 12.0 m2/g and a pore volume of at least 0.015 cm3/g, said
CaO having a sorption capacity of at least about 70 grams of CO2
per kilogram of CaO.
[0012] The CaO may be provided in any usable form including, but
not limited to, pellets, granules, fines, monoliths and
combinations thereof. The CaO may be obtained by processing
chicken eggshells.
[0013] Although the regeneration of CaO step may be performed
any functional process, it is preferred that it is conducted by
a process selected from the group consisting of: (a) calcining
in the presence of steam and/or CO2 and/or H2 with O2, and/or
synthesis gas with O2 and/or under partial vacuum or
combinations thereof; (b) a process in which the heat is added
to the calciner using steam and a combination of calciner fuel
and oxidant; (c) a process in which the calciner fuel is H2 or
natural gas or synthesis gas or coal or combinations thereof;
(d) a process in which the oxidant is air or oxygen or
combinations thereof; (e) a process in which heat is provided to
the calciner directly or indirectly; (f) calciner reactor
temperatures ranging from about 700-1100 C; and (a process for
adjusting the calciner temperature by modifying the CaO to CaCO3
ratio in the calciner. The gas phase product from the calciner
may comprise pure CO2 and could also contain trace amounts of
H2S.
[0014] The disclosed embodiments also includes a process for
producing hydrogen, comprising the steps of: (a) reforming a
gaseous hydrocarbon fuel in the presence of CaO and steam to
remove CO2, sulfur and halide contaminants in the form of H2S,
COS and HX, where X is a halide, in a solid-phase
calcium-containing product comprising CaCO3, CaS and CaX2,
thereby producing a mixture of CO and hydrogen; (b) separating
the solid-phase calcium-containing product from an enriched
gaseous hydrogen product; and (c) regenerating the CaO by
calcining the solid-phase calcium-containing product at a
condition selected from the group consisting of: in the presence
of steam, in the presence of CO2, in the presence of synthesis
gas, in the presence of H2 and O2, under partial vacuum, and
combinations thereof.
[0015] The gaseous fuel may be natural gas, C1-C4 hydrocarbons,
or mixtures thereof. The reforming step may involve the
introduction of CO2, so called dry reforming.
[0016] The reforming step may involve a reforming catalyst.
Suitable reforming catalysts include those comprising: Ni, Pt,
Rh, Pd, Ru, W, Mo, their oxide or carbides or sulfides. The
reforming catalyst may use a support. Suitable supports for use
with the foregoing reforming or pre-reforming catalysts include:
alumina, silica, titania, zirconia, and combinations thereof. It
is preferred that the reforming catalyst is sulfur intolerant.
[0017] The reforming operation may occur in a temperature range
of from about 550 to about 750 C. and at a pressure in the range
of from about 1 to about 60 atm. Preferably, it operates in the
temperature range of from about 600 to about 70[deg.] C. and at
a pressure in the range of from about 20 to about 30 atm.
[0018] The enriched hydrogen product produced may be as pure as
99.9% when 3* the stoichiometric requirement of steam is used
and 95% pure when the stoichiometric requirement of steam is
used.
[0019] This process may additionally comprise the step of: (d)
recycling at least a portion of a product stream from a
Fischer-Tropsch reactor, fed by the reformer, so as to introduce
a chemical species selected from the group consisting of:
methane, C1-C4 hydrocarbons, CO, hydrogen and combinations
thereof back into the reformer.
[0020] In all embodiments, the CaO may have a surface area of at
least 12.0 m2/g and a pore volume of at least 0.015 cm3/g, said
CaO having a sorption capacity of at least about 70 grams of CO2
per kilogram of CaO.
[0021] The CaO may be provided in any usable form including, but
not limited to, pellets, granules, fines, monoliths and
combinations thereof. The CaO may be obtained by processing
chicken eggshells.
[0022] When a catalyst is used the enriched hydrogen product may
achieve 99.99% purity when 3* the stoichiometric requirement of
steam is used. The enriched hydrogen product may achieve 98%
purity when the stoichiometric requirement of steam is used.
Some embodiments may attain a purity of at least 80% with a
maximum sulfur (H2S/COS) concentration of less than 10 ppm when
3* the stoichiometric requirement of steam is used and at least
70% purity with a maximum sulfur concentration of less than 1
ppm when the stoichiometric requirement of steam is used. The
process allows for a hydrogen purity of at least 80% with a
maximum sulfur (H2S/COS) concentration of less than 10 ppm when
3* the stoichiometric requirement of steam is used and at least
70% purity with a maximum sulfur concentration of less than 1
ppm when the stoichiometric requirement of steam is used.
[0023] Another process of the disclosed embodiments for
producing hydrogen, comprising the steps of: (a) at least
partially oxidizing a fuel into a raw gas comprising CO,
hydrogen, steam and sulfur and halide contaminants in the form
of H2S, COS and HX, where X is a halide; (b) passing the raw gas
through a water gas shift reactor (WGSR) into which CaO and
steam are injected, the CaO reacting with the shifted gas to
remove CO2, sulfur and halides in a solid-phase
calcium-containing product comprising CaCO3, CaS and CaX2; (c)
separating the solid-phase calcium-containing product from an
enriched gaseous hydrogen product; and (d) regenerating the CaO
by calcining the solid-phase calcium-containing product at a
condition selected from the group consisting of: in the presence
of steam, in the presence of CO2, in the presence of synthesis
gas, in the presence of H2 and O2, under partial vacuum, and
combinations thereof.
[0024] In all embodiments, the CaO may have a surface area of at
least 12.0 m2/g and a pore volume of at least 0.015 cm3/g, said
CaO having a sorption capacity of at least about 70 grams of CO2
per kilogram of CaO.
[0025] The CaO may be provided in any usable form including, but
not limited to, pellets, granules, fine, monoliths and
combinations thereof. The CaO may be obtained by processing
chicken eggshells.
[0026] Although the steam may be injected into the WGSR in any
functional quantity, it is preferred that the steam injected is
in the range of from about the stoichiometric requirement to
about 3 times the stoichiometric requirement.
[0027] The WGSR may be of a type selected from the group
consisting of: fixed bed reactors, fluidized bed reactors,
entrained flow reactors, moving bed reactors rotary kilns, or
combinations thereof. Additionally, the calcinations step may be
performed in a calcinations reactor of a type selected from the
group consisting of: fixed bed reactors, fluidized bed reactors,
entrained flow reactors, moving bed reactors rotary kilns, or
combinations thereof.
[0028] In some embodiments, the WGSR does not have a catalyst
disposed therein. As such the WGSR operates at a temperature in
the range of from about 550-750 C, in the pressure range of from
about 1 to about 60 atm, it is preferred that the WGSR reactor
operate in a temperature range of from about 600-700 C and at a
pressure in the range of from about 20 to about 30 atm. In some
embodiments, the enriched hydrogen product is 99% pure when 3
times the stoichiometric steam requirement is used. At the
stoichiometric steam requirement the process produces an
enriched hydrogen product that is 90% pure. In another catalytic
embodiment, the enriched hydrogen product has a H2/Co ratio of
at least 2.5 and a maximum sulfur (H2S/COS) concentration of
less than 10 ppm using only the stoichiometric requirement of
steam.
[0029] In some embodiments, a catalyst may be used in the WGSR.
A suitable high temperature shift catalyst which may include:
Fe, Cu, Co, Mo, W, Cs, Pt, Ph, Pd, and other precious metal
catalysts or their oxides or sulfides or combinations thereof.
Suitable supports for use with the foregoing high temperature
shift catalysts include: Cr2O3, ZnO, MgO, ceria, alumina,
silica, zirconia and combinations thereof.
[0030] A WGSR reactor with a catalyst operates in the
temperature range of from about 550-750 C and at a pressure in
the range of from about 1 to about 100 atm. It is preferred that
the WGSR reactor operate in the temperature range of from about
600-700 C and at a pressure of from about 20 to about 30 atm.
When a catalyst is used the enriched hydrogen product may
achieve 99.99% purity when 3* the stoichiometric requirement of
steam is used in the WGSR. The enriched hydrogen product may
achieve 98% purity when the stoichiometric requirement of steam
is used. Some embodiments may attain a purity of at least 80%
with a maximum sulfur (H2S/COS) concentration of less than 10
ppm when 3* the stoichiometric requirement of steam is used and
at least 70% purity with a maximum sulfur concentration of less
than 1 ppm when the stoichiometric requirement of steam is
used...
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Processes", Int. J. Hydrogen Energy. 1996, 21, 349-365.
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for a Range of Hydrogen Production Processes". Int. J. Hydrogen
Energy. 1998, 23, 653-659.
Roark, S. E.; Mackay, R.; Sammells, A. F. "Hydrogen Separation
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International Technical Conference on Coal Utilization &
Fuel Systems. 2002, 27 (Vol. 1), 101-112.
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Dioxide Sorbents for Fluidized Bed Coal Combustion Using
Thermogravimetric Analysis". Thermochimica Acta. 1978, 26,
241-255.
Stiegel, Gary J.; Ramezan, Massood. "Hydrogen from Coal
Gasification: An Economical Pathway to a Sustainable Energy
Future". International Journal of Coal Geology. 2006, 65,
173-190.
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Burnt Lime" Trans. Society of Min. Eng of AIME. 1973, 254,
28-33.
Wei, S-H.; Mahuli, S. K.; Agnihotri, R.; Fan, L-S. "High Surface
Area Calcium Carbonate: Pore Structural Properties and Sulfation
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Pennline, H. W. "Separation and Capture of CO2 from Large
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Waste Manage. Assoc. 2003, 53, 645-715.
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Removal of SO2 in the Presence of High-Concentration CO2 at High
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http://www.netl.doe.gov/publications/proceedings/01/carbon_seq/2b2.pdf.
CONVERSION
OF CARBONACEOUS FUELS INTO CARBON FREE ENERGY CARRIERS
WO2010037011
[ PDF ]
A system for converting fuel is provided and includes a first
reactor comprising a plurality of ceramic composite particles,
the ceramic composite particles comprising at least one metal
oxide disposed on a support, wherein the first reactor is
configured to reduce the at least one metal oxide with a fuel to
produce a reduced metal or a reduced metal oxide; a second
reactor configured to oxidize at least a portion of the reduced
metal or reduced metal oxide from the said first reactor to
produce a metal oxide intermediate; a source of air; and a third
reactor communicating with said source of air and configured to
regenerate the at least one metal oxide from the remaining
portion of the solids discharged from the said first reactor and
the solids discharged from the said second reactor by oxidizing
the metal oxide intermediate.
The present invention is generally directed to systems and
methods of converting carbonaceous fuels. Reduction- Oxidation
(redox) reactions, with the presence of one or more chemical
intermediates, are generally utilized to convert the
carbonaceous fuels.
In order to meet the ever increasing demand for clean and
affordable energy carriers and to ensure the sustainable growth
of modern economy, efficient and environmentally friendly
technologies that convert carbonaceous fuels such as coal, crude
oil, natural gas, biomass, tar sands, and oil shale into carbon
free energy carriers are highly desirable. An energy carrier is
a substance or phenomenon that can be used to produce mechanical
work or heat or to operate chemical or physical processes.
Existing carbonaceous fuel conversion technologies are either
capital intensive (gasification or ultra-supercritical
pulverized coal combustion), have low efficiencies (sub-
critical pulverized coal combustion), or both, especially when
CO2 regulation is mandatory.
Chemical reactions between carbonaceous fuels and air/steam/CO2
through the assistance of a metal oxide medium may represent an
effective way to convert the fuels. A number of techniques have
been proposed to convert carbonaceous fuels using metal oxide.
For example, Watkins, U.S. Patent No. 3,027,238, describes a
method for producing hydrogen gas including reducing a metal
oxide in a reducing zone, and oxidizing the reduced metal with
steam to produce hydrogen in an oxidizing zone. Thomas et al.,
U.S. Published Application No. 2005/0175533, and Fan et al., PCT
Application No. WO 2007/082089, both describe methods for
producing hydrogen gas by reducing a metal oxide in a reduction
reaction between a carbon-based fuel and a metal oxide to
provide a reduced metal or metal oxide having a lower oxidation
state, and oxidizing the reduced metal or metal oxide to produce
hydrogen and a metal oxide having a higher oxidation state. The
metal or metal oxide is provided in the form of a porous
composite of a ceramic material containing the metal or metal
oxide. A well known process is a steam-iron process wherein
coal-derived producer gas is reacted with iron oxide particles
to be later regenerated with steam to produce hydrogen gas.
However, a fluidized bed is used in this system which causes
iron (Fe) to loop between FeO and Fe3U4, the gas is not fully
converted, and no pure gas stream can be produced. Ishida et
al., U.S. Patent No. 5,447,024, describes processes that make
use of nickel oxide particles to convert natural gas through a
chemical looping process into heat to be used in a turbine.
However, this technology has limited applicability because it
can only convert costly natural gas into heat/electricity.
Therefore, both the feedstock and the product of the process are
restricted.
With increasing demand for cleaner and more efficient energy
carriers such as electricity, hydrogen, and fuels, the need
arises for improved systems, and system components therein,
which produce the aforementioned energy carriers with higher
efficiency and lower emissions.
Embodiments of the present invention provide novel systems and
processes for converting solid, liquid, and gaseous fuels into
efficient energy carriers. In one embodiment, a system for
converting solid, liquid, or gaseous fuel is provided and
comprises a first reactor comprising a plurality of ceramic
composite particles. The ceramic composite particles comprise at
least one metal oxide disposed on a support, and the first
reactor is configured to reduce the at least one metal oxide
with a fuel to produce a reduced metal or a reduced metal oxide.
The system includes a second reactor configured to at least
partially re-oxidize the reduced metal or reduced metal oxide to
produce a metal oxide intermediate. The system also includes a
source of air and a third reactor communicating with the source
of air and configured to regenerate the at least one metal oxide
by oxidizing the metal oxide intermediate. In a preferred form,
the fuel is a solid fuel or a gaseous fuel. Optionally, a fuel
conversion enhancement gas, preferably including CO2, steam,
and/or H2, is sent to the first reactor in which the gas flows
countercurrently to the flow of solids. Also provided is a
method of preparing ceramic composite particles, for example in
the form of pellets, comprising the steps of, mixing a metal
oxide with at least one ceramic material to form a mixture,
granulating the mixture, and drying the granulated mixture. The
dried, granulated mixture is processed into particle form such
that the characteristic length of the particles is greater than
about 200 [mu]m. The particles are heat treated at a temperature
of from about 500 to about 1500<0>C and optionally may be
reduced and oxidized prior to use in the reactor system.
METHODS
AND SYSTEMS FOR SYNTHESIZING IRON-BASED MATERIALS AND
SEQUESTERING CARBON DIOXIDE
WO2010132784
[ PDF ]
Methods and systems for sequestering carbon dioxide and
generating hydrogen are disclosed. In some embodiments, the
methods include the following: dissolving an iron based material
that includes a carbonate-forming element into a solution
including the carbonate-forming element and iron; increasing a
pH of the solution to cause precipitation of iron oxide from the
solution thereby generating a first source of Fe2O3; reacting
the carbonate-forming element in the solution with a first
source of carbon dioxide to produce a carbonate thereby
sequestering the carbon dioxide; oxidizing the first source of
Fe2O3 with a carbonaceous fuel thereby generating a second
source of carbon dioxide and iron; and oxidizing the iron with
steam thereby generating hydrogen and an iron oxide. Some
embodiments include producing iron-based catalysts.
BACKGROUND
[0002] Since the industrial revolution, the amount of CO2 in the
atmosphere has risen from 280 ppm in 1800 to 370 ppm in 2000,
mainly due to the consumption of fossil fuels. More than half of
the energy used in the United States comes from the use of coal,
and it is mostly used to generate electricity. Unfortunately,
CO2 is one of the greenhouse gases considered to be responsible
for global warming. Moreover, the increased atmospheric CO2
concentration will acidify the ocean and will change the
chemistry of the surface ocean, leading to a potentially
detrimental impact on the ecosystem. In order to meet the ever-
increasing global energy demands, while stabilizing the
atmospheric CO2 level, current carbon emissions should be
significantly reduced.
[0003] There have been significant research and development
activities in the area of carbon capture and storage (CCS),
including a number of integrated technologies (e.g., chemical
looping processes) to combine CO2 capture with
electricity/chemical/fuel production. Chemical looping processes
involve a sorbent, typically a metal, or more likely a low
oxidation state metal oxide that can be oxidized in air. The
oxide is reduced by carbonaceous fuels in a subsequent step. A
variation of this approach oxidizes the metal not in air but in
a chemical reaction with steam to produce a pure stream of H2.
The chemical looping processes also allow the inherent
generation of the sequestration-ready CO2 stream at higher
pressures.
[0004] Once captured, CO2 can be stored via geological
sequestration, ocean disposal, mineral carbonation, and
biological fixation. The mineral sequestration scheme is
particularly attractive, since this process converts CO2 into
thermodynamically stable carbonates via the reaction of CO2 with
widely available non-carbonate minerals, such as serpentine and
olivine. Therefore, the mineral sequestration process eliminates
the risk of accidental CO2 releases. The reaction underlining
mineral carbonation mimics natural chemical transformations of
CO2, such as the weathering of rocks. The main challenges of
this storage method have been the slow dissolution kinetics and
large energy requirement associated with the mineral processing.
SUMMARY
[0005] The previously developed pH swing carbon mineral
sequestration immobilizes the gaseous CO2 into a
thermodynamically stable solid, MgCO3, using Mg-bearing minerals
such as serpentine. This mineral carbonation technology is
particularly promising since it generates value-added solid
products: high surface area silica, iron oxide, and magnesium
carbonate, while providing a safe and permanent storage option
for CO2. By carefully controlling the pH of the system, these
solids products can be produced with high purity. The disclosed
subject matter focuses on the synthesis of iron oxide particles
as a chemical looping sorbent in order to achieve the
integration between carbon capture and storage technologies. The
synthesized iron-based chemical looping sorbent has been found
to be as effective as commercially available iron oxide
nanoparticles at converting syngas/carbonaceous fuel into high
purity H2, while producing a sequestration-ready CO2 stream.
[0006] The disclosed subject matter utilizes the iron component
of magnesium-bearing minerals, e.g., olivine and serpentine,
during carbon mineral sequestration. These minerals often
contain 5-10 percent by weight of iron, and the recovery and
utilization of iron during the mineral processing increases the
economic feasibility of carbon mineral sequestration technology.
Among many applications of iron-based materials, the disclosed
subject matter focuses on the synthesis of iron-based chemical
looping sorbents, which can be used for carbon dioxide capture
and hydrogen production, as well as the syntheses of iron-based
catalysts to be used in the production of synthetic liquid fuels
and hydrogen from carbonaceous materials including coal,
biomass, and municipal solid wastes...
CALCIUM
LOOPING PROCESS FOR HIGH PURITY HYDROGEN PRODUCTION
INTERGRATED WITH CAPTURE OF CARBON DIOXIDE, SULFUR AND
HALIDE
WO2010045232
[ PDF ]
A process for producing hydrogen comprising the steps of: (i)
gasifying a fuel into a raw synthesis gas comprising CO,
hydrogen, steam, sulfur and halide contaminants in the form of
H2S, COS, and HX, wherein X is a halide; (ii) passing the raw
synthesis gas through a water gas shift reactor (WGSR) into
which CaO and steam are injected, the CaO reacting with the
shifted gas to remove CO2, sulfur and halides in a solid-phase
calcium-containing product comprising CaCO3, CaS and CaX2; (iii)
separating the solid-phase calcium-containing product from an
enriched gaseous hydrogen product; and (iv) regenerating the CaO
by calcining the solid-phase calcium-containing product at a
condition selected from the group consisting of: in the presence
of steam, in the presence of CO2, in the presence of synthesis
gas, in the presence of H2 and O2, under partial vacuum, and
combinations thereof.
BACKGROUND
OF THE ART AND SUMMARY OF EXEMPLARY EMBODIMENTS OF THE
INVENTION
[0004] The production of gaseous hydrogen, and particularly,
gaseous hydrogen of high purity, is known in the prior art. A
variety of feedstocks are known to be useful for these
processes, including petroleum, coal, biomass, oil sands, coke,
tar, wax oil shales, or combinations of these materials.
Depending upon the feedstock selected, the amount of sulfur and
halogens present in the feedstock can vary extensively, and many
considerations, including catalyst poisoning and the cost of
environmental control equipment can be effected by these
specific contaminants. [0005] Also, the process used will affect
the amount of carbon dioxide produced. As carbon dioxide is
associated with global warming, emissions of carbon dioxide must
be controlled. [0006] It is therefore an unmet advantage of the
prior art to provide a process of this type wherein the carbon
dioxide, sulfur and halides are captured as a part of the
hydrogen production process.
[0007] The rising energy demand coupled with the depleting
global oil reserves and the environmental degradation due to
emissions has led to extensive research in the field of clean
energy production. The total energy use, globally, has been
predicted to increase from 421 quadrillion BTU in 2003 to 722
quadrillion BTU in 2030. <l> In the United States, the
annual energy consumption is projected to increase by 71% from
2003 to 2030, which is much higher than the predicted increase
in the domestic energy production. Currently, the United States
is dependent on foreign oil for 56% of its energy needs. This
translates to the fact that although the production capacity of
petroleum products and natural gas will increase, the US will be
dependent on foreign oil for 70% of its energy needs by 2025.
<l> On the other front, the energy related CO2 emission
has increased at an annual average percentage of 1.3 % in the
past decade and is projected by the EIA to increase at the same
rate till 2030. To add to this, oil prices are expected to soar
up by 50 % at the end of 2030. <l> Hence, the
implementation of energy generation technologies as well as
production of "Green" fuels which will reduce the dependence on
oil, limit the emissions of CO2, sulfur and other pollutants and
be economically feasible are the need of the hour.
[0008] This need has led to a global push towards the
development of efficient, economical, and reliable carbon
capture and sequestration technologies (CCS) for application to
fossil fuel based power plants. Coal is present in abundance,
about 494 billion tons of reserves in the United States, within
which the state of Ohio has 5% or 24 billion tons of reserves.
While it gives rise to harmful emissions it can be used to
provide a major portion of our energy needs if CCS is
implemented in a carbon constrained scenario. The implementation
of CO2 capture could be through post combustion capture,
oxy-combustion and pre-combustion. These technologies could be
applied to either coal, natural gas or biomass based systems.
Figure 1 illustrates these concepts through simplified flow
diagrams.
[0009] Post combustion capture technology involves the
combustion of coal or natural gas to produce hot flue gas which
is used to generate steam. The CO2 from the flue gas is then
captured using solvents or sorbents. Although coal combustion
for power generation is economically viable in a non - carbon
constrained scenario, this will not be true when a CO2
regulation is applied. This is because the combustion of coal or
natural gas results in the production of large volumes of flue
gas in which the CO2 concentration is very low (13-14% for coal
combustion and 3-4% for natural gas combustion) and hence the
capture of CO2 becomes inefficient and expensive. Addition of
CO2 capture results in plant efficiency losses of 8-12 %
resulting in a net efficiency of 35% for a Super Critical
Pulverized Coal Combustion (SC-PCC) plant on an LHV
basis.<2> In oxy-combustion, the fuel is burnt in oxygen
and recycled flue gas, to produce a concentrated stream
containing CO2 and H2O which is then dried, compressed and
transported for sequestration. Although oxy-combustion obviates
the need for a separate CO2 capture stage, it requires an Air
Separation Unit (ASU) which is energy intensive and expensive.
Oxy-combustion also yields in an overall LHV efficiency of 35 %
for an SC-PCC plant similar to the post combustion capture
case.<2> Pre combustion capture involves the gasification
of coal or the reforming of natural gas to produce syngas. The
syngas is then cleaned and sent to shift reactors (WGSR) to
convert the carbon monoxide to H2 and CO2 in the presence of
steam. The CO2 is then captured from the shifted syngas and the
H2 is either combusted to produce electricity or purified in a
Pressure Swing Absorber (PSA) and used for the production of
chemicals and liquid fuels. The overall efficiency of an IGCC
plant with CO2 capture is 38-40% which is higher than that for
post combustion and oxy-combustion systems.<2>
[0010] Pre-combustion capture technologies are a potential
solution to efficient and economical CCS implementation as
gasification results in the production of a lower level of
criteria pollutants when compared to combustion and the
application of CCS to gasification systems is more efficient and
economical when compared to CCS for post combustion systems. It
has been estimated that with the implementation of CCS using
solvent based systems, the increase in the COE for an IGCC is 25
to 40 % while that for PC boilers is 60 to 85%. In a carbon
constrained scenario, it has been estimated that the cost of a
super critical PC boiler will be $2140/KWe while that of an IGCC
will be $1890/KWe. In addition to being more economical and
efficient, gasification is also very versatile and capable of
producing H2 and liquid fuels in addition to
electricity.<3>
[0011] Applying CO2 capture to coal gasification requires the
addition of shift reactors, a CO2 separation process and CO2
compression and drying. In a typical gasification system, coal
is partially oxidized in the presence of steam and oxygen to
produce syngas which is then converted to H2, electricity or
liquid fuels.
[0012] Coal Gasification: CxHy + H2O = xCO + (Vi + I) H2 (1)
[0013] For the implementation of CCS, the CO in syngas needs to
be converted to H2 and CO2 via the WGS reaction so that a large
fraction of the carbon content can be captured.
[0014] WGS reaction: CO + H2O = CO2 + H2 (2)
[0015] In the conventional scenario, a series of shift reactors
with catalysts and excess steam addition is used due to the
thermodynamic limitation of the WGS reaction. Depending on the
sulfur tolerance of the catalyst, the WGSR can be conducted as a
raw syngas (sour) shift or the clean syngas (sweet) shift.
Commercially the clean WGSR is carried out in two stages: the
high and low temperature shift reactors using iron oxide and
copper catalysts respectively. The high temperature shift is
conducted to convert the bulk of the carbon monoxide to H2 due
to the fast kinetics. The lower temperature shift reaction is
carried out as the equilibrium conversion is higher at lower
temperatures but the gas stream has to be cooled down to 210
C-240 C which makes the process, energy inefficient.<4>
Further, the commercial iron oxide catalyst has a sulfur
tolerance of only about 100 ppm and the copper catalyst has a
lower tolerance to sulfur (<0.1 ppm) and chloride impurities.
Hence syngas clean up is required upstream of the shift reactors
to remove sulfur, chloride and other impurities and downstream
of the shift operation to remove CO2. Cleanup is achieved using
conventional scrubbing technology which is energy intensive due
to the cooling and heating requirements. The sour gas shift uses
a sulfided catalyst which is resistant to high sulfur
concentrations in the syngas stream and operates at a
temperature of 250- 500C. By using the raw gas shift, sulfur
removal and CO2 removal can be conducted down stream of the
shift reactor in an integrated mode. However the extent of CO
conversion is lower in the raw gas shift than in the clean gas
shift. Addition of the CO2 capture step results in a 25 - 40%
increase in the cost of electricity (COE), 7.2% decrease in the
efficiency, 2.1% due to CO2 compression and 0.9% due to CO2
capture.<3>
[0016] Conventional pre-combustion capture in a natural gas
based plant involves methane reforming which is conducted at
temperatures greater than 900C and is highly energy
intensive.<5>
[0017] Steam Methane Reforming (SMR): CH4 + H2O = CO + 3H2 (3)
[0018] The syngas obtained is then shifted similar to the
operation in the IGCC system and CO2 capture is achieved at low
temperatures using physical (eg. selexol, rectisol, chilled
ammonia) or chemical (eg. amine solutions) solvents resulting in
a large increase in the parasitic energy requirement and related
cost of energy. Hence there is a need to improve the energy
efficiency and economics by implementing process intensification
to reduce the foot print and improve the heat integration within
the system. [0019] The Calcium Looping Process (CLP) developed
at the Ohio State University<6>, as illustrated in Figures
2 and 3, improves the efficiency of the coal/natural gas to H2
process by integrating various unit operations into a single
stage. The CLP not only aids in curbing CO2 emissions but also
improves the efficiency and reduces the CO2 foot print. It
utilizes a high temperature regenerable CaO sorbent which in
addition to capturing the CO2, enhances the yield of H2 and
simultaneously captures sulfur and halide impurities. It also
enhances the yield of liquid fuels by reforming the lighter
hydrocarbons and unconverted syngas into hydrogen which is used
to increase the H2:C0 ratio in the syngas to 2 and for
hydrotreating the liquid fuel. [0020] Figure 2 depicts the
integration of the CLP in a coal gasification system. Syngas
obtained from coal gasification is sent through a particulate
capture device to the integrated H2 production reactor. When CaO
is injected into the syngas it reacts with the CO2, H2S, COS and
HCl to form a mixture containing predominantly CaCO3 and small
amounts of calcium sulfide and calcium chloride. The insitu
removal of CO2 removes the equilibrium limitation of the WGS
reaction thereby obviating the need for a catalyst and excess
steam addition. The CaCO3 is subsequently calcined to yield a
pure CO2 stream for sequestration and the CaO is recycled back.
In this process, naturally occurring limestone which is cheap
and abundantly available is used and its capture capacity is
maintained at 12.5 moles CO2/Kg of CaO over multiple cycles
which is significantly larger than other solvents and sorbents.
Thus the CLP integrates several unit operations, such as the
WGSR, CO2 capture system, sulfur removal and halide removal in
one process module. Figure 3 shows the integration of the CLP in
a natural gas reforming process in which the unit operations
namely, reforming, WGS, CO2 capture and sulfur removal are
integrated in a single reactor system. Within the H2 production
reactor, the natural gas is reformed with steam in the presence
of the reforming catalyst and CaO sorbent. The removal of CO2
removes the thermodynamic limitation of the WGSR and the
reforming reaction and results in a high conversion of the
methane to H2. The H2 production reactor is heat neutral due to
the exothermic energy from the WGS and carbonation reactions
being equal to the endothermic reforming reaction heat duty.
Hence the temperature of operation for the reforming reaction
can be reduced from over 900C to 650C. The spent sorbent
containing CaCO3, CaO and CaS is separated from the H2 and
regenerated in a calciner to produce a sequestration ready CO2
stream. The CaO sorbent is then recycled back to the integrated
H2 production reactor. [0021] The overall objectives of the CLP
are to improve process efficiency and economics by process
intensification, produce H2 for electricity generation,
chemicals and liquid fuels synthesis with integrated carbon and
contaminants capture at high temperatures, produce a
sequestration ready CO2 stream, reduce excess steam requirement
and obviate the need for a WGS catalyst. Experimental
investigation in a bench scale facility reveals that high purity
H2 of 99.7% purity with less that 1 ppm sulfur impurity can be
produced. Process evaluation using ASPEN Plus(R) software
suggests that the overall efficiency of the coal to H2 process
integrated with the CLP is 64% (HHV) which is significantly
higher than 57% (HHV) achieved by the state-of-the-art H2 from
coal process...
METHODS
AND SYSTEMS FOR SYNTHESIZING IRON-BASED MATERIALS AND
SEQUESTERING CARBON DIOXIDE
WO2010132784
[ PDF ]
Methods and systems for sequestering carbon dioxide and
generating hydrogen are disclosed. In some embodiments, the
methods include the following: dissolving an iron based material
that includes a carbonate-forming element into a solution
including the carbonate-forming element and iron; increasing a
pH of the solution to cause precipitation of iron oxide from the
solution thereby generating a first source of Fe2O3; reacting
the carbonate-forming element in the solution with a first
source of carbon dioxide to produce a carbonate thereby
sequestering the carbon dioxide; oxidizing the first source of
Fe2O3 with a carbonaceous fuel thereby generating a second
source of carbon dioxide and iron; and oxidizing the iron with
steam thereby generating hydrogen and an iron oxide. Some
embodiments include producing iron-based catalysts.
BACKGROUND
[0002] Since the industrial revolution, the amount of CO2 in the
atmosphere has risen from 280 ppm in 1800 to 370 ppm in 2000,
mainly due to the consumption of fossil fuels. More than half of
the energy used in the United States comes from the use of coal,
and it is mostly used to generate electricity. Unfortunately,
CO2 is one of the greenhouse gases considered to be responsible
for global warming. Moreover, the increased atmospheric CO2
concentration will acidify the ocean and will change the
chemistry of the surface ocean, leading to a potentially
detrimental impact on the ecosystem. In order to meet the ever-
increasing global energy demands, while stabilizing the
atmospheric CO2 level, current carbon emissions should be
significantly reduced.
[0003] There have been significant research and development
activities in the area of carbon capture and storage (CCS),
including a number of integrated technologies (e.g., chemical
looping processes) to combine CO2 capture with
electricity/chemical/fuel production. Chemical looping processes
involve a sorbent, typically a metal, or more likely a low
oxidation state metal oxide that can be oxidized in air. The
oxide is reduced by carbonaceous fuels in a subsequent step. A
variation of this approach oxidizes the metal not in air but in
a chemical reaction with steam to produce a pure stream of H2.
The chemical looping processes also allow the inherent
generation of the sequestration-ready CO2 stream at higher
pressures.
[0004] Once captured, CO2 can be stored via geological
sequestration, ocean disposal, mineral carbonation, and
biological fixation. The mineral sequestration scheme is
particularly attractive, since this process converts CO2 into
thermodynamically stable carbonates via the reaction of CO2 with
widely available non-carbonate minerals, such as serpentine and
olivine. Therefore, the mineral sequestration process eliminates
the risk of accidental CO2 releases. The reaction underlining
mineral carbonation mimics natural chemical transformations of
CO2, such as the weathering of rocks. The main challenges of
this storage method have been the slow dissolution kinetics and
large energy requirement associated with the mineral processing.
SUMMARY
[0005] The previously developed pH swing carbon mineral
sequestration immobilizes the gaseous CO2 into a
thermodynamically stable solid, MgCO3, using Mg-bearing minerals
such as serpentine. This mineral carbonation technology is
particularly promising since it generates value-added solid
products: high surface area silica, iron oxide, and magnesium
carbonate, while providing a safe and permanent storage option
for CO2. By carefully controlling the pH of the system, these
solids products can be produced with high purity. The disclosed
subject matter focuses on the synthesis of iron oxide particles
as a chemical looping sorbent in order to achieve the
integration between carbon capture and storage technologies. The
synthesized iron-based chemical looping sorbent has been found
to be as effective as commercially available iron oxide
nanoparticles at converting syngas/carbonaceous fuel into high
purity H2, while producing a sequestration-ready CO2 stream.
[0006] The disclosed subject matter utilizes the iron component
of magnesium-bearing minerals, e.g., olivine and serpentine,
during carbon mineral sequestration. These minerals often
contain 5-10 percent by weight of iron, and the recovery and
utilization of iron during the mineral processing increases the
economic feasibility of carbon mineral sequestration technology.
Among many applications of iron-based materials, the disclosed
subject matter focuses on the synthesis of iron-based chemical
looping sorbents, which can be used for carbon dioxide capture
and hydrogen production, as well as the syntheses of iron-based
catalysts to be used in the production of synthetic liquid fuels
and hydrogen from carbonaceous materials including coal,
biomass, and municipal solid wastes...
CARBONATION
CALCINATION REACTION PROCESS FOR CO2 CAPTURE USING A HIGHLY
REGENERABLE SORBENT
US2011286902
A process for the efficient capture of CO2 and sulfur from
combustion flue gas streams and gasification based fuel gas
mixtures using regenerable and recyclable calcium based
sorbents. The regeneration of the calcium sorbent is
accomplished by hydrating the sorbent at high temperatures of
about 600 DEG C. and a pressure higher than 6 bars to lower the
parasitic energy consumption.
BACKGROUND
AND SUMMARY OF THE INVENTION
[0003] The concept of utilizing lime for carbon dioxide capture
has existed for well over a century. It was first introduced by
DuMotay and Marechal in 1869 for enhancing the gasification of
coal using lime followed by CONSOL's CO2 acceptor process a
century later when this concept was tested in a 40 tons/day
plant. A variation of this process called the Hypring process
was developed in Japan for the production of hydrogen at high
pressures. Harrison et al. and Grace et al. have also applied
this concept to the production of hydrogen both from Syngas by
the water gas shift reaction and methane by the sorption
enhanced steam methane reforming reaction. Silaban et al.
studied the reversibility of the carbonation reaction for the
production of hydrogen.
[0004] Within the last decade research has also focused on the
use of lime for carbon dioxide capture from combustion flue gas.
Shimizu et al. conceptually designed a process that uses
twin-fluidized bed reactors for capturing carbon dioxide from a
coal combustion power plant. After the conceptual design, a
significant amount of research has advanced the concept greatly.
The contribution of John R. Grace from the University of British
Columbia, Juan Carlos Abanades from Instituto Nacional del
Carbon-CSIC and CANMET energy Technology Centre have further
enhanced the understanding of the Chemical Looping Technology
using lime sorbent for the capture of CO2. In addition, the
reversibility of the carbonation reaction, the investigation of
the decay of CO2 capture over multiple cycles of carbonation and
calcination and the production layer formation have been studied
by Barker et al., Bhatia and Perlmutter and Mess et al.
respectively.
[0005] The regenerability of the calcium oxide sorbent has been
the major draw back of high temperature calcium based CO2
capture processes. CaO oxide sorbents are prone to sintering
during to the regeneration step which is conducted at high
temperatures. Over multiple cycles sintering progressively
increases and reduces the CO2 capture capacity of the sorbent.
Sintering results in an increase in solid circulation and make
up rate. Research has been conducted to develop methods of
reducing the sintering of the sorbent. Pretreatment methods have
been developed at the CANMET Energy Center which involves
hydration of the calcined sorbent at 100[deg.] C. at atmospheric
pressure and saturation pressure, powdering the sorbent and
preheating the sorbent in a nitrogen atmosphere. The sintering
of the sorbent was reduced when these pretreatment methods were
applied to the sorbent. This concept developed by CANMET Energy
Center is only a pretreatment method and is applied to the
sorbent once in 20 cycles and sorbent sintering still occurs
resulting in a reduction in CO2 capture capacity. This concept
has been tested by Manovic et al. in TGA, fixed bed and a 75
KWth dual fluidized bed combustion plant.
[0006] Grace et al. have also investigated the pretreatment of
the sorbent by hydration at atmospheric pressure at 150[deg.] C.
and 300[deg.] C. From thermodynamics it is seen that complete
hydration does not occur spontaneously at temperature of
300[deg.] C. and hence complete reactivation of the sorbent is
not achieved by these methods. In addition, this method has also
been developed to be applied once in a few cycles and hence
sorbent degradation still occurs.
[0007] The reactivation of the sorbent by recarbonation has also
been investigated but this process requires an additional
calcination step which is very energy consuming and
uneconomical.
[0008] Zeeman et al. have integrated the hydration process as a
reactivation step in the CO2 removal process. They hydrate the
sorbent at 300[deg.] C. in the presence of CO2 and steam at
atmospheric pressure. There has been no mention about the extent
of hydration achieved by this process and the amount of
carbonation occurring during the hydration process. Although
this method was found to reduce sintering and reactivate the
sorbent a steady decline in the reactivity of the sorbent was
still observed.
[0009] Consequently, it can be understood that there is a need
for a cost effective and efficient system and method to minimize
the sintering of the selected sorbent and overcome the sorbents
decay in reactivity. Exemplary systems and methods of the
inventive concept satisfy these needs/preferences.
SUMMARY OF
THE INVENTIVE CONCEPT
[0010] Exemplary embodiments of the present invention are
directed to economically feasible options for the integration of
calcium sorbent based CO2 capture technology in post-combustion
systems, specifically in coal-fired power plants. Exemplary
embodiments described herein may also be applicable for
pre-combustion systems. Exemplary embodiments of the inventive
concept specifically provide process integration options while
factoring in such variables as location(s) of flue/fuel gas
drawn for CO2 capture, source of steam for the hydrator, solids
purge and recycle locations, particle capture devices (PCDs),
reactor configurations, heat management, and a variety of other
factors.
[0011] In contrast to the above mentioned methods of sorbent
reactivation. The Ohio State University has developed a process
to completely reactivate the sorbent in an energy efficient
manner using pressure hydration. The complete reactivation of
the sorbent during every cycle reverses the effect of sintering
and the history of the number of cycles is completely lost.
Hence, this process minimizes the amount of solids circulation
in the system. In addition, pressure hydration of the sorbent
may be conducted at high temperatures of 600[deg.] C. and the
exothermic energy of hydration is used to supply the endothermic
energy of dehydration. In addition, pressure hydration does not
require the cooling and reheating of the sorbent thereby
reducing the parasitic energy consumption of the process.
Extensive experiments have been conducted at the Ohio State
University wherein complete regeneration of the sorbent has been
observed for a number of cycles. Pressure hydration as used
herein does not require saturation pressure or high pressure of
operation. A pressure of above 6 bar is sufficient for a
temperature of 600[deg.] C. As the temperature decreases the
pressure required is also reduced. Thus, the hydration process
proposed by the Ohio state University is energy efficient and
economical.
[0012] Embodiments of the present invention detail a process for
the efficient capture of CO2 and sulfur from combustion flue gas
streams and gasification based fuel gas mixtures using
regenerable and recyclable calcium based sorbents. In exemplary
embodiments, the solid sorbent is predominantly a metal oxide
that can be converted into a hydrate. Some exemplary embodiments
specifically provide a method of reactivating the sorbent by
hydrating it at a high temperature of about 600[deg.] C. and a
pressure higher than about 6 bars in order to lower the
parasitic energy consumption of the process. In other exemplary
embodiments, hydration occurs at temperatures high enough such
that heat generated from exothermic reaction can be extracted to
generate steam for a steam turbine or used for heat exchange;
minimum of at least 300[deg.] C. and greater for steam turbine
integration. At higher hydration temperatures, greater than
about 500[deg.] C., process efficiency increases, but hydration
must operate at pressures greater than 1 atm. At temperatures
between about 300[deg.] C. to about 500[deg.] C. hydration may
occur at about 1 atmosphere. More specifically, temperature from
between 350[deg.] C. and about 512[deg.] C. By hydrating the
sorbent at high temperatures the energy loss due to solids
heating and cooling can be avoided and most crucially the
exothermic energy of hydration can be used to provide the energy
required for the dehydration of the sorbent or to generate high
quality steam for additional electricity generation. At high
temperatures of 600[deg.] C., the hydration reaction proceeds to
completion only at pressures higher than 6 bars and hence the
hydration is conducted at high pressures.
[0013] In other exemplary embodiments at different temperatures
of sorbent hydration, the pressure must also be adjusted to
maintain maximum reactivity. This reactivation procedure which
follows the calcination step during every carbonation
calcination cycle produces a high capacity regenerable sorbent
which aids in lowering the total amount of solids in circulation
making the CO2 capture process economically attractive...
INTEGRATION
OF REFORMING/WATER SPLITTING AND ELECTROCHEMICAL SYSTEMS FOR
POWER GENERATION WITH INTEGRATED CARBON CAPTURE
WO2011031755
[ PDF ]
High efficiency electricity generation processes and systems
with substantially zero CO2 emissions are provided. A closed
looping between the unit that generates gaseous fuel (H2, CO,
etc) and the fuel cell anode side is formed. In certain
embodiments, the heat and exhaust oxygen containing gas from the
fuel cell cathode side are also utilized for the gaseous fuel
generation. The systems for converting fuel may comprise
reactors configured to conduct oxidation- reduction reactions.
The resulting power generation efficiencies are improved due to
the minimized steam consumption for the gaseous fuel
production.in the fuel cell anode loop as well as the strategic
mass and energy integration schemes.
The present invention is generally directed to systems and
methods of electricity generation with in-situ CO2 capture. In
certain embodiments, a reduction- oxidation (redox) system using
one or more chemical intermediates is utilized to convert
carbonaceous fuel with C([3/4] capture. This is followed by
strategic integration with an electrochemical conversion device
to produce electricity. In other embodiments, water splitting
systems are integrated with the electrochemical systems. Through
the process integrations, the process auxiliary power
consumption and/or water utilization and energy used for steam
generation are minimized.
Fossil fuels including crude oil, natural gas, and coal
represent the majority of today's energy supply worldwide. The
use of fossil fuels, however, requires that they be transformed
to a carrier such as heat, electricity, liquid fuels, or
chemicals through chemical conversion processes. With an
increasing energy demand and concomitant concerns over the
carbon emissions from fossil fuel usage, extensive efforts have
been geared toward developing carbon neutral, efficient and
economical energy systems that are sustainable. A transition
from the use of fossil fuels to that of nuclear and renewable
resources such as solar and biomass, thus, represents the
natural progression of such efforts. Existing electricity
generation technologies have one or more of the following
limitations/drawbacks: 1) high costs (e.g., photovoltaic,
gasification, ultra- supercritical pulverized coal combustion);
2) low efficiency (e.g., sub-critical pulverized coal
combustion); 3) environmental concerns (e.g., fossil fuel power
plants); and 4) safety concerns (e.g., nuclear power). One of
the common issues with respect to a conventional thermal power
plant is the large amount of exergy loss during cooling and
reheating of steam. A system and method that minimizes the
requirements for steam generation is thus desirable.
Chemical reactions between carbonaceous fuels and air/steam/C02
through the assistance of a reaction medium may represent an
effective way to minimize exergy loss in the fuel conversion
process. A number of techniques have been proposed to convert
carbonaceous fuels using metal oxide. For example, Watkins, U.S.
Patent No. 3,027,238, describes a method for producing hydrogen
gas including reducing a metal oxide in a reducing zone, and
oxidizing the reduced metal with steam to produce hydrogen in an
oxidizing zone. This technique, however, is limited to gaseous
fuel conversion. Moreover, the gaseous fuel is only partially
converted by the metal oxide. Thomas, US Patent No. 7,767,191;
Fan, PCT Application No. WO 2007082089; and Fan, PCT Application
No. WO 2010037011 describe methods for producing hydrogen gas by
reducing a metal oxide in a reduction reaction between a
carbon-based fuel and a metal oxide to provide a reduced metal
or metal oxide having a lower oxidation state, and oxidizing the
reduced metal or metal oxide to produce hydrogen and a metal
oxide having a higher oxidation state.
Hydrogen can also be produced from water splitting through
photoelectrolysis, thermolysis, and thermochemical routes. To
produce electricity, the aforementioned processes teach the
further conversion of the hydrogen product in a gas turbine, gas
engine, and/or fuel cell. However, a large amount of steam is
used in these processes for hydrogen generation. Simple
conversion of hydrogen in conventional hydrogen fueled power
generation devices will lead to cooling and reheating of large
amounts of steam/water, resulting in a large irreversibility of
the power generation system.
With increasing demand for electricity, the need arises for
improved processes, systems, and system components therein,
which produce electricity with higher efficiency and fewer
pollutants.
Embodiments of the present invention are generally directed to
high efficiency electricity generation processes and systems
with substantially zero CO2 emissions. A closed loop between the
unit that generates gaseous fuel (H2, CO, etc.) and the fuel
cell anode side is formed. In certain embodiments, the heat and
exhaust oxygen containing gas from the fuel cell cathode side
are also utilized for the gaseous fuel generation. The power
generation efficiencies of the systems disclosed herein are
significantly greater than state-of-the-art approaches due to
the minimized steam consumption for the gaseous fuel production,
in the fuel cell anode loop, as well as the strategic mass and
energy integration schemes...
SYNTHETIC
FUELS AND CHEMICALS PRODUCTION WITH IN-SITU CO2 CAPTURE
WO2011031752
[ PDF ]
Novel redox based systems for fuel and chemical production with
in- situ CO2 capture are provided. A redox system using one or
more chemical intermediates is utilized in conjunction with
liquid fuel generation via indirect Fischer-Tropsch synthesis,
direct hydro genation, or pyrolysis. The redox system is used to
generate a hydrogen rich stream and/or CO2 and/or heat for
liquid fuel and chemical production. A portion of the byproduct
fuels and/or steam from liquid fuel and chemical synthesis is
used as part of the feedstock for the redox system
The present invention is generally directed to systems and
methods for synthetic fuels and chemical products generation
with in-situ C02 capture. A reduction- oxidation (redox) system
using one or more chemical intermediates is generally utilized
in conjunction with liquid fuel generation via indirect C02
hydrogenation, direct hydrogenation, or pyrolysis.
Fossil fuels including crude oil, natural gas, and coal provide
more than 85% of today's energy supply. These fossil fuels are
usually transformed to carriers such as electricity and liquid
transportation fuels prior to utilization by end consumers.
Electricity is mainly produced by relatively abundant energy
sources such as coal, natural gas, and nuclear. In contrast,
liquid transportation fuel is almost exclusively obtained from
crude oil, whose supply is relatively insecure with volatile
prices. With an increasing energy demand and concomitant
concerns over carbon emissions from fossil fuel usage,
affordable synthetic transportation fuels from more abundant
resources such as coal, biomass, and oil shale are desirable. To
address the environmental concerns, the next generation
synthetic fuel production processes need to be able to capture
pollutants generated in the process. These pollutants include
C02, sulfur compounds, and mercury, among others.
Synthetic fuel is generated from gaseous fuels such as natural
gas through reforming and the Fischer- Tropsch ("F-T") scheme.
Solid fuels such as coal, biomass, and pet coke can be converted
to synthetic fuel through indirect liquefaction (gasification -
water gas shift - Fischer- Tropsch), direct liquefaction, or
pyrolysis. These systems are, however, more capital intensive
than oil refining processes. Moreover, their energy conversion
efficiencies are relatively low.
Synthetic fuel can also be generated from biomass via
biochemical routes.
However, a large amount of process water is utilized. Moreover,
the biochemical approaches have stringent requirements on the
feedstock.
All the aforementioned processes involve C02 emissions. C02
capture from these processes associates with notable energy
losses and hence decreases in process efficiency. Embodiments of
the present invention provide alternatives to produce synthetic
fuel from naturally occurring carbonaceous fuel sources with
high efficiency and effective C02 capture.
Embodiments of the present invention are generally directed to
novel redox based systems for fuel and chemical production with
in-situ C02 capture. A redox system using one or more chemical
intermediates is generally utilized in conjunction with liquid
fuel generation via indirect Fischer- Tropsch synthesis, direct
hydrogenation, or pyrolysis. The redox system is used to
generate a hydrogen rich stream and/or C02 and/or heat for
liquid fuel and chemical production. A portion of the byproduct
fuels and/or steam from liquid fuel and chemical synthesis is
used as part of the feedstock for the redox system.
SYSTEMS
FOR CONVERTING FUEL
WO2012155054
Technical
Background
There is a constant need for clean and efficient energy
generation systems. Most of the commercial processes that
generate energy carriers such as steam, hydrogen, synthesis gas
(syngas), liquid fuels and/or electricity are based on fossil
fuels. Furthermore, the dependence on fossil fuels is expected
to continue in the foreseeable future due to the much lower
costs compared to renewable sources. Currently, the conversion
of carbonaceous fuels such as coal, natural gas, petroleum coke
is usually conducted through a combustion or reforming process.
However, combustion of carbonaceous fuels, especially coal, is a
carbon intensive process that emits large quantities of carbon
dioxide to the environment. Sulfur and nitrogen compounds are
also generated in this process due to the complex content in
coal.
Chemical reactions between metal oxides and carbonaceous fuels,
on the other hand, may provide a better way to recover the
energy stored in the fuels. Several processes are based on the
reaction of metal oxide particles with carbonaceous fuels to
produce useful energy carriers. For example, Ishida et al. U.S.
Pat. No. 5,447,024 describes processes wherein nickel oxide
particles are used to convert natural gas through a chemical
looping process into heat, which may be used in a turbine.
However, recyclability of pure metal oxides is poor and
constitutes an impediment for its use in commercial and
industrial processes. Moreover, this technology has limited
applicability, because it may only convert natural gas, which is
more costly than other fossil fuels. Another well known process
is a steam-iron process, wherein coal derived producer gas is
reacted with iron oxide particles in a fhiidized bed reactor to
be later regenerated with steam to produce hydrogen gas. This
process however suffers from poor gas conversion rates due to
improper contact between reacting solids and gases, and is
incapable of producing a hydrogen rich stream.
As demands increase for cleaner and more efficient systems of
converting fuel, the need arises for improved systems, and
system components therein, which will convert fuel effectively,
while reducing pollutants.
The concepts of the present disclosure are generally applicable
to systems for producing hydrogen from coal, or other
carbonaceous fuels. In accordance with one embodiment of the
present disclosure, a system for converting fuel may comprise a
first moving bed reactor, a second reactor, and a non-mechanical
valve. The first moving bed reactor may comprise at least one
tapered section and multiple injection gas ports. The multiple
injection gas ports may be configured to deliver a fuel to the
first moving bed reactor. The first moving bed reactor may be
configured to reduce an oxygen carrying material with a fuel by
defining a countercurrent flowpath for the fuel relative to the
oxygen carrying material. The second reactor may communicate
with the first moving bed reactor and may be operable to receive
an oxygen source. The second reactor may be configured to
regenerate the reduced oxygen carrying material by oxidation.
The non-mechanical valve may comprise a circuitous piping
assembly disposed between the first moving bed reactor and the
second reactor. At least one gas opening may be configured to
receive a gas stream. The gas stream may be operable to reduce
gas leakage between the first moving bed reactor and the second
reactor...
OXYGEN
CARRYING MATERIALS
WO2012155059
In accordance with one embodiment of the present disclosure, an
oxygen carrying material may include a primary active mass, a
primary support material, and a secondary support material. The
oxygen carrying material may include about 20% to about 70% by
weight of the primary active mass, the primary active mass
including a composition having a metal or metal oxide selected
from the group consisting of Fe, Co, Ni, Cu, Mo, Mn, Sn, Ru, Rh,
and combinations thereof. The oxygen carrying material may
include about 5% to about 70% by weight of a primary support
material. The oxygen carrying material may include about 1% to
about 35% by mass of a secondary support material.
OXYGEN
CARRYING MATERIALS
This application claims the benefit of prior-filed U.S.
Provisional Patent Application Ser. No. 61/484,982, filed May
11, 2011, the subject matter of which is hereby incorporated by
reference in its entirety. The present invention relates to
oxygen carrying materials, and specifically to oxygen carrying
materials that are associated with chemical looping systems.
There is a constant need for clean and efficient energy
generation systems. Most of the commercial processes that
generate energy carriers such as steam, hydrogen, synthesis gas
(syngas), liquid fuels and/or electricity are based on fossil
fuels. Furthermore, the dependence on fossil fuels is expected
to continue in the foreseeable future due to the lower costs
compared to renewable sources. Currently, the conversion of
carbonaceous fuels such as coal, natural gas, and petroleum coke
is usually conducted through a combustion or reforming process.
However, combustion of carbonaceous fuels, especially coal, is a
carbon intensive process that emits large quantities of carbon
dioxide to the environment. Sulfur and nitrogen compounds are
also generated in this process due to the complex content in
coal.
Traditionally the chemical energy stored inside coal has been
utilized by combustion with 02, with C02 and H20 as products.
Similar reactions can be carried out if instead of oxygen, an
oxygen carrying material is used in a chemical looping process.
For example, metal oxides such as Fe203 can act as suitable
oxygen carrying materials. However, unlike combustion of fuel
with air, there is a relatively pure sequestration ready C02
stream produced on combustion with metal oxide carriers. The
reduced form of metal oxide may then be reacted with air to
liberate heat to produce electricity or reacted with steam to
form a relatively pure stream of hydrogen, which can then be
used for a variety of purposes.
Chemical reactions between metal oxides and carbonaceous fuels,
on the other hand, may provide a better way to recover the
energy stored in the fuels. Several processes are based on the
reaction of metal oxide particles with carbonaceous fuels to
produce useful energy carriers. For example, Ishida et al. (U.S.
Pat. No. 5,447,024) describes processes wherein nickel oxide
particles are used to convert natural gas through a chemical
looping process into heat, which may be used in a turbine.
However, recyclability of pure metal oxides is poor and
constitutes an impediment for its use in commercial and
industrial processes. Moreover, this technology has limited
applicability, because it can only convert natural gas, which is
more costly than other fossil fuels. Another well known process
is a steam-iron process, wherein coal derived producer gas is
reacted with iron oxide particles in a fluidized bed reactor to
be later regenerated with steam to produce hydrogen gas. This
process however suffers from poor gas conversion rates due to
improper contact between reacting solids and gases, and is
incapable of producing a hydrogen rich stream.
One of the problems with the prior art in combustion looping
systems has been the metal/metal oxide oxygen carrying material.
For example, iron in the form of small particles may degrade and
break up in the reactor. Iron oxide has little mechanical
strength as well. After only a few redox cycles, the activity
and oxygen carrying capacity of the metal/metal oxide may
decline considerably. Replacing the oxygen carrying material
with additional fresh metal/metal oxide makes the process more
costly.
As demands increase for cleaner and more efficient systems of
converting fuel, the need arises for improved systems, and
system components therein, which will convert fuel effectively,
while reducing pollutants.
The concepts of the present disclosure are generally applicable
to oxygen carrying materials. In accordance with one embodiment
of the present disclosure, an oxygen carrying material may
comprise a primary active mass, a primary support material, and
a secondary support material. The oxygen carrying material may
comprise about 20% to about 70% by weight of the primary active
mass, the primary active mass comprising a composition having a
metal or metal oxide selected from the group consisting of Fe,
Co, Ni, Cu, Mo, Mn, Sn, Ru, Rh, and combinations thereof. The
oxygen carrying material may comprise about 5% to about 70% by
weight of a primary support material. The primary support
material may comprise a composition having at least one metal,
metal oxide, metal carbide, metal nitrate, metal halide, or
combinations thereof; at least one ceramic or clay material, or
salts thereof; at least one naturally occurring ore; or
combinations thereof. The oxygen carrying material may comprise
about 1% to about 35% by mass of a secondary support material.
The secondary support material may comprise a composition having
at least one metal, metal oxide, metal carbide, metal nitrate,
metal halide, or combinations thereof; at least one ceramic or
clay material or salts thereof; at least one naturally occurring
ore; or combinations thereof. The primary support material
composition and the secondary support material composition may
be different. In accordance with another embodiment of the
present disclosure, a system for converting fuel may comprise an
oxygen carrying material, a first reactor comprising a moving
bed and an inlet for providing fuel to the first reactor,
wherein the first reactor is configured to reduce the oxygen
carrying material with the fuel to produce a reduced oxygen
carrying material, and a second reactor communicating with the
first reactor and an oxygen source, wherein the second reactor
is configured to regenerate the oxygen carrying material by
oxidizing the oxygen carrying material.
In accordance with another embodiment of the present disclosure,
a method for synthesizing an oxygen carrying material may
include forming a matrix comprising a primary active mass, a
primary support, and a secondary support; drying the matrix; and
forming the matrix into particles of the oxygen carrying
material...
CARBONATION
CALCINATION REACTION PROCESS FOR CO2 CAPTURE USING A HIGHLY
REGENERABLE SORBENT
US2011286902
[ PDF ]
A process for the efficient capture of CO2 and sulfur from
combustion flue gas streams and gasification based fuel gas
mixtures using regenerable and recyclable calcium based
sorbents. The regeneration of the calcium sorbent is
accomplished by hydrating the sorbent at high temperatures of
about 600 DEG C. and a pressure higher than 6 bars to lower the
parasitic energy consumption.
BACKGROUND AND
SUMMARY OF THE INVENTION
[0003] The concept of utilizing lime for carbon dioxide capture
has existed for well over a century. It was first introduced by
DuMotay and Marechal in 1869 for enhancing the gasification of
coal using lime followed by CONSOL's CO2 acceptor process a
century later when this concept was tested in a 40 tons/day
plant. A variation of this process called the Hypring process
was developed in Japan for the production of hydrogen at high
pressures. Harrison et al. and Grace et al. have also applied
this concept to the production of hydrogen both from Syngas by
the water gas shift reaction and methane by the sorption
enhanced steam methane reforming reaction. Silaban et al.
studied the reversibility of the carbonation reaction for the
production of hydrogen.
[0004] Within the last decade research has also focused on the
use of lime for carbon dioxide capture from combustion flue gas.
Shimizu et al. conceptually designed a process that uses
twin-fluidized bed reactors for capturing carbon dioxide from a
coal combustion power plant. After the conceptual design, a
significant amount of research has advanced the concept greatly.
The contribution of John R. Grace from the University of British
Columbia, Juan Carlos Abanades from Instituto Nacional del
Carbon-CSIC and CANMET energy Technology Centre have further
enhanced the understanding of the Chemical Looping Technology
using lime sorbent for the capture of CO2. In addition, the
reversibility of the carbonation reaction, the investigation of
the decay of CO2 capture over multiple cycles of carbonation and
calcination and the production layer formation have been studied
by Barker et al., Bhatia and Perlmutter and Mess et al.
respectively.
[0005] The regenerability of the calcium oxide sorbent has been
the major draw back of high temperature calcium based CO2
capture processes. CaO oxide sorbents are prone to sintering
during to the regeneration step which is conducted at high
temperatures. Over multiple cycles sintering progressively
increases and reduces the CO2 capture capacity of the sorbent.
Sintering results in an increase in solid circulation and make
up rate. Research has been conducted to develop methods of
reducing the sintering of the sorbent. Pretreatment methods have
been developed at the CANMET Energy Center which involves
hydration of the calcined sorbent at 100[deg.] C. at atmospheric
pressure and saturation pressure, powdering the sorbent and
preheating the sorbent in a nitrogen atmosphere. The sintering
of the sorbent was reduced when these pretreatment methods were
applied to the sorbent. This concept developed by CANMET Energy
Center is only a pretreatment method and is applied to the
sorbent once in 20 cycles and sorbent sintering still occurs
resulting in a reduction in CO2 capture capacity. This concept
has been tested by Manovic et al. in TGA, fixed bed and a 75
KWth dual fluidized bed combustion plant.
[0006] Grace et al. have also investigated the pretreatment of
the sorbent by hydration at atmospheric pressure at 150[deg.] C.
and 300[deg.] C. From thermodynamics it is seen that complete
hydration does not occur spontaneously at temperature of
300[deg.] C. and hence complete reactivation of the sorbent is
not achieved by these methods. In addition, this method has also
been developed to be applied once in a few cycles and hence
sorbent degradation still occurs.
[0007] The reactivation of the sorbent by recarbonation has also
been investigated but this process requires an additional
calcination step which is very energy consuming and
uneconomical.
[0008] Zeeman et al. have integrated the hydration process as a
reactivation step in the CO2 removal process. They hydrate the
sorbent at 300[deg.] C. in the presence of CO2 and steam at
atmospheric pressure. There has been no mention about the extent
of hydration achieved by this process and the amount of
carbonation occurring during the hydration process. Although
this method was found to reduce sintering and reactivate the
sorbent a steady decline in the reactivity of the sorbent was
still observed.
[0009] Consequently, it can be understood that there is a need
for a cost effective and efficient system and method to minimize
the sintering of the selected sorbent and overcome the sorbents
decay in reactivity. Exemplary systems and methods of the
inventive concept satisfy these needs/preferences.
SUMMARY OF
THE INVENTIVE CONCEPT
[0010] Exemplary embodiments of the present invention are
directed to economically feasible options for the integration of
calcium sorbent based CO2 capture technology in post-combustion
systems, specifically in coal-fired power plants. Exemplary
embodiments described herein may also be applicable for
pre-combustion systems. Exemplary embodiments of the inventive
concept specifically provide process integration options while
factoring in such variables as location(s) of flue/fuel gas
drawn for CO2 capture, source of steam for the hydrator, solids
purge and recycle locations, particle capture devices (PCDs),
reactor configurations, heat management, and a variety of other
factors.
[0011] In contrast to the above mentioned methods of sorbent
reactivation. The Ohio State University has developed a process
to completely reactivate the sorbent in an energy efficient
manner using pressure hydration. The complete reactivation of
the sorbent during every cycle reverses the effect of sintering
and the history of the number of cycles is completely lost.
Hence, this process minimizes the amount of solids circulation
in the system. In addition, pressure hydration of the sorbent
may be conducted at high temperatures of 600[deg.] C. and the
exothermic energy of hydration is used to supply the endothermic
energy of dehydration. In addition, pressure hydration does not
require the cooling and reheating of the sorbent thereby
reducing the parasitic energy consumption of the process.
Extensive experiments have been conducted at the Ohio State
University wherein complete regeneration of the sorbent has been
observed for a number of cycles. Pressure hydration as used
herein does not require saturation pressure or high pressure of
operation. A pressure of above 6 bar is sufficient for a
temperature of 600[deg.] C. As the temperature decreases the
pressure required is also reduced. Thus, the hydration process
proposed by the Ohio state University is energy efficient and
economical.
[0012] Embodiments of the present invention detail a process for
the efficient capture of CO2 and sulfur from combustion flue gas
streams and gasification based fuel gas mixtures using
regenerable and recyclable calcium based sorbents. In exemplary
embodiments, the solid sorbent is predominantly a metal oxide
that can be converted into a hydrate. Some exemplary embodiments
specifically provide a method of reactivating the sorbent by
hydrating it at a high temperature of about 600[deg.] C. and a
pressure higher than about 6 bars in order to lower the
parasitic energy consumption of the process. In other exemplary
embodiments, hydration occurs at temperatures high enough such
that heat generated from exothermic reaction can be extracted to
generate steam for a steam turbine or used for heat exchange;
minimum of at least 300[deg.] C. and greater for steam turbine
integration. At higher hydration temperatures, greater than
about 500[deg.] C., process efficiency increases, but hydration
must operate at pressures greater than 1 atm. At temperatures
between about 300[deg.] C. to about 500[deg.] C. hydration may
occur at about 1 atmosphere. More specifically, temperature from
between 350[deg.] C. and about 512[deg.] C. By hydrating the
sorbent at high temperatures the energy loss due to solids
heating and cooling can be avoided and most crucially the
exothermic energy of hydration can be used to provide the energy
required for the dehydration of the sorbent or to generate high
quality steam for additional electricity generation. At high
temperatures of 600[deg.] C., the hydration reaction proceeds to
completion only at pressures higher than 6 bars and hence the
hydration is conducted at high pressures.
[0013] In other exemplary embodiments at different temperatures
of sorbent hydration, the pressure must also be adjusted to
maintain maximum reactivity. This reactivation procedure which
follows the calcination step during every carbonation
calcination cycle produces a high capacity regenerable sorbent
which aids in lowering the total amount of solids in circulation
making the CO2 capture process economically attractive...
INTEGRATION
OF REFORMING/WATER SPLITTING AND ELECTROCHEMICAL SYSTEMS FOR
POWER GENERATION WITH INTEGRATED CARBON CAPTURE
WO2011031755
[ PDF ]
High efficiency electricity generation processes and systems
with substantially zero CO2 emissions are provided. A closed
looping between the unit that generates gaseous fuel (H2, CO,
etc) and the fuel cell anode side is formed. In certain
embodiments, the heat and exhaust oxygen containing gas from the
fuel cell cathode side are also utilized for the gaseous fuel
generation. The systems for converting fuel may comprise
reactors configured to conduct oxidation- reduction reactions.
The resulting power generation efficiencies are improved due to
the minimized steam consumption for the gaseous fuel
production.in the fuel cell anode loop as well as the strategic
mass and energy integration schemes.
The present invention is generally directed to systems and
methods of electricity generation with in-situ CO2 capture. In
certain embodiments, a reduction- oxidation (redox) system using
one or more chemical intermediates is utilized to convert
carbonaceous fuel with C([3/4] capture. This is followed by
strategic integration with an electrochemical conversion device
to produce electricity. In other embodiments, water splitting
systems are integrated with the electrochemical systems. Through
the process integrations, the process auxiliary power
consumption and/or water utilization and energy used for steam
generation are minimized.
Fossil fuels including crude oil, natural gas, and coal
represent the majority of today's energy supply worldwide. The
use of fossil fuels, however, requires that they be transformed
to a carrier such as heat, electricity, liquid fuels, or
chemicals through chemical conversion processes. With an
increasing energy demand and concomitant concerns over the
carbon emissions from fossil fuel usage, extensive efforts have
been geared toward developing carbon neutral, efficient and
economical energy systems that are sustainable. A transition
from the use of fossil fuels to that of nuclear and renewable
resources such as solar and biomass, thus, represents the
natural progression of such efforts. Existing electricity
generation technologies have one or more of the following
limitations/drawbacks: 1) high costs (e.g., photovoltaic,
gasification, ultra- supercritical pulverized coal combustion);
2) low efficiency (e.g., sub-critical pulverized coal
combustion); 3) environmental concerns (e.g., fossil fuel power
plants); and 4) safety concerns (e.g., nuclear power). One of
the common issues with respect to a conventional thermal power
plant is the large amount of exergy loss during cooling and
reheating of steam. A system and method that minimizes the
requirements for steam generation is thus desirable.
Chemical reactions between carbonaceous fuels and air/steam/C02
through the assistance of a reaction medium may represent an
effective way to minimize exergy loss in the fuel conversion
process. A number of techniques have been proposed to convert
carbonaceous fuels using metal oxide. For example, Watkins, U.S.
Patent No. 3,027,238, describes a method for producing hydrogen
gas including reducing a metal oxide in a reducing zone, and
oxidizing the reduced metal with steam to produce hydrogen in an
oxidizing zone. This technique, however, is limited to gaseous
fuel conversion. Moreover, the gaseous fuel is only partially
converted by the metal oxide. Thomas, US Patent No. 7,767,191;
Fan, PCT Application No. WO 2007082089; and Fan, PCT Application
No. WO 2010037011 describe methods for producing hydrogen gas by
reducing a metal oxide in a reduction reaction between a
carbon-based fuel and a metal oxide to provide a reduced metal
or metal oxide having a lower oxidation state, and oxidizing the
reduced metal or metal oxide to produce hydrogen and a metal
oxide having a higher oxidation state.
Hydrogen can also be produced from water splitting through
photoelectrolysis, thermolysis, and thermochemical routes. To
produce electricity, the aforementioned processes teach the
further conversion of the hydrogen product in a gas turbine, gas
engine, and/or fuel cell. However, a large amount of steam is
used in these processes for hydrogen generation. Simple
conversion of hydrogen in conventional hydrogen fueled power
generation devices will lead to cooling and reheating of large
amounts of steam/water, resulting in a large irreversibility of
the power generation system.
With increasing demand for electricity, the need arises for
improved processes, systems, and system components therein,
which produce electricity with higher efficiency and fewer
pollutants.
Embodiments of the present invention are generally directed to
high efficiency electricity generation processes and systems
with substantially zero CO2 emissions. A closed loop between the
unit that generates gaseous fuel (H2, CO, etc.) and the fuel
cell anode side is formed. In certain embodiments, the heat and
exhaust oxygen containing gas from the fuel cell cathode side
are also utilized for the gaseous fuel generation. The power
generation efficiencies of the systems disclosed herein are
significantly greater than state-of-the-art approaches due to
the minimized steam consumption for the gaseous fuel production,
in the fuel cell anode loop, as well as the strategic mass and
energy integration schemes...
SYNTHETIC
FUELS AND CHEMICALS PRODUCTION WITH IN-SITU CO2 CAPTURE
WO2011031752
Novel redox based systems for fuel and chemical production with
in- situ CO2 capture are provided. A redox system using one or
more chemical intermediates is utilized in conjunction with
liquid fuel generation via indirect Fischer-Tropsch synthesis,
direct hydro genation, or pyrolysis. The redox system is used to
generate a hydrogen rich stream and/or CO2 and/or heat for
liquid fuel and chemical production. A portion of the byproduct
fuels and/or steam from liquid fuel and chemical synthesis is
used as part of the feedstock for the redox system
The present invention is generally directed to systems and
methods for synthetic fuels and chemical products generation
with in-situ C02 capture. A reduction- oxidation (redox) system
using one or more chemical intermediates is generally utilized
in conjunction with liquid fuel generation via indirect C02
hydrogenation, direct hydrogenation, or pyrolysis.
Fossil fuels including crude oil, natural gas, and coal provide
more than 85% of today's energy supply. These fossil fuels are
usually transformed to carriers such as electricity and liquid
transportation fuels prior to utilization by end consumers.
Electricity is mainly produced by relatively abundant energy
sources such as coal, natural gas, and nuclear. In contrast,
liquid transportation fuel is almost exclusively obtained from
crude oil, whose supply is relatively insecure with volatile
prices. With an increasing energy demand and concomitant
concerns over carbon emissions from fossil fuel usage,
affordable synthetic transportation fuels from more abundant
resources such as coal, biomass, and oil shale are desirable. To
address the environmental concerns, the next generation
synthetic fuel production processes need to be able to capture
pollutants generated in the process. These pollutants include
C02, sulfur compounds, and mercury, among others.
Synthetic fuel is generated from gaseous fuels such as natural
gas through reforming and the Fischer- Tropsch ("F-T") scheme.
Solid fuels such as coal, biomass, and pet coke can be converted
to synthetic fuel through indirect liquefaction (gasification -
water gas shift - Fischer- Tropsch), direct liquefaction, or
pyrolysis. These systems are, however, more capital intensive
than oil refining processes. Moreover, their energy conversion
efficiencies are relatively low.
Synthetic fuel can also be generated from biomass via
biochemical routes.
However, a large amount of process water is utilized. Moreover,
the biochemical approaches have stringent requirements on the
feedstock.
All the aforementioned processes involve C02 emissions. C02
capture from these processes associates with notable energy
losses and hence decreases in process efficiency. Embodiments of
the present invention provide alternatives to produce synthetic
fuel from naturally occurring carbonaceous fuel sources with
high efficiency and effective C02 capture.
Embodiments of the present invention are generally directed to
novel redox based systems for fuel and chemical production with
in-situ C02 capture. A redox system using one or more chemical
intermediates is generally utilized in conjunction with liquid
fuel generation via indirect Fischer- Tropsch synthesis, direct
hydrogenation, or pyrolysis. The redox system is used to
generate a hydrogen rich stream and/or C02 and/or heat for
liquid fuel and chemical production. A portion of the byproduct
fuels and/or steam from liquid fuel and chemical synthesis is
used as part of the feedstock for the redox system...
SYSTEMS
FOR CONVERTING FUEL
WO2012155054
Technical Background
There is a constant need for clean and efficient energy
generation systems. Most of the commercial processes that
generate energy carriers such as steam, hydrogen, synthesis gas
(syngas), liquid fuels and/or electricity are based on fossil
fuels. Furthermore, the dependence on fossil fuels is expected
to continue in the foreseeable future due to the much lower
costs compared to renewable sources. Currently, the conversion
of carbonaceous fuels such as coal, natural gas, petroleum coke
is usually conducted through a combustion or reforming process.
However, combustion of carbonaceous fuels, especially coal, is a
carbon intensive process that emits large quantities of carbon
dioxide to the environment. Sulfur and nitrogen compounds are
also generated in this process due to the complex content in
coal.
Chemical reactions between metal oxides and carbonaceous fuels,
on the other hand, may provide a better way to recover the
energy stored in the fuels. Several processes are based on the
reaction of metal oxide particles with carbonaceous fuels to
produce useful energy carriers. For example, Ishida et al. U.S.
Pat. No. 5,447,024 describes processes wherein nickel oxide
particles are used to convert natural gas through a chemical
looping process into heat, which may be used in a turbine.
However, recyclability of pure metal oxides is poor and
constitutes an impediment for its use in commercial and
industrial processes. Moreover, this technology has limited
applicability, because it may only convert natural gas, which is
more costly than other fossil fuels. Another well known process
is a steam-iron process, wherein coal derived producer gas is
reacted with iron oxide particles in a fhiidized bed reactor to
be later regenerated with steam to produce hydrogen gas. This
process however suffers from poor gas conversion rates due to
improper contact between reacting solids and gases, and is
incapable of producing a hydrogen rich stream.
As demands increase for cleaner and more efficient systems of
converting fuel, the need arises for improved systems, and
system components therein, which will convert fuel effectively,
while reducing pollutants.
The concepts of the present disclosure are generally applicable
to systems for producing hydrogen from coal, or other
carbonaceous fuels. In accordance with one embodiment of the
present disclosure, a system for converting fuel may comprise a
first moving bed reactor, a second reactor, and a non-mechanical
valve. The first moving bed reactor may comprise at least one
tapered section and multiple injection gas ports. The multiple
injection gas ports may be configured to deliver a fuel to the
first moving bed reactor. The first moving bed reactor may be
configured to reduce an oxygen carrying material with a fuel by
defining a countercurrent flowpath for the fuel relative to the
oxygen carrying material. The second reactor may communicate
with the first moving bed reactor and may be operable to receive
an oxygen source. The second reactor may be configured to
regenerate the reduced oxygen carrying material by oxidation.
The non-mechanical valve may comprise a circuitous piping
assembly disposed between the first moving bed reactor and the
second reactor. At least one gas opening may be configured to
receive a gas stream. The gas stream may be operable to reduce
gas leakage between the first moving bed reactor and the second
reactor...
BACKGROUND
AND SUMMARY OF THE INVENTION
[0003] The concept of utilizing lime for carbon dioxide capture
has existed for well over a century. It was first introduced by
DuMotay and Marechal in 1869 for enhancing the gasification of
coal using lime followed by CONSOL's CO2 acceptor process a
century later when this concept was tested in a 40 tons/day
plant. A variation of this process called the Hypring process
was developed in Japan for the production of hydrogen at high
pressures. Harrison et al. and Grace et al. have also applied
this concept to the production of hydrogen both from Syngas by
the water gas shift reaction and methane by the sorption
enhanced steam methane reforming reaction. Silaban et al.
studied the reversibility of the carbonation reaction for the
production of hydrogen.
[0004] Within the last decade research has also focused on the
use of lime for carbon dioxide capture from combustion flue gas.
Shimizu et al. conceptually designed a process that uses
twin-fluidized bed reactors for capturing carbon dioxide from a
coal combustion power plant. After the conceptual design, a
significant amount of research has advanced the concept greatly.
The contribution of John R. Grace from the University of British
Columbia, Juan Carlos Abanades from Instituto Nacional del
Carbon-CSIC and CANMET energy Technology Centre have further
enhanced the understanding of the Chemical Looping Technology
using lime sorbent for the capture of CO2. In addition, the
reversibility of the carbonation reaction, the investigation of
the decay of CO2 capture over multiple cycles of carbonation and
calcination and the production layer formation have been studied
by Barker et al., Bhatia and Perlmutter and Mess et al.
respectively.
[0005] The regenerability of the calcium oxide sorbent has been
the major draw back of high temperature calcium based CO2
capture processes. CaO oxide sorbents are prone to sintering
during to the regeneration step which is conducted at high
temperatures. Over multiple cycles sintering progressively
increases and reduces the CO2 capture capacity of the sorbent.
Sintering results in an increase in solid circulation and make
up rate. Research has been conducted to develop methods of
reducing the sintering of the sorbent. Pretreatment methods have
been developed at the CANMET Energy Center which involves
hydration of the calcined sorbent at 100[deg.] C. at atmospheric
pressure and saturation pressure, powdering the sorbent and
preheating the sorbent in a nitrogen atmosphere. The sintering
of the sorbent was reduced when these pretreatment methods were
applied to the sorbent. This concept developed by CANMET Energy
Center is only a pretreatment method and is applied to the
sorbent once in 20 cycles and sorbent sintering still occurs
resulting in a reduction in CO2 capture capacity. This concept
has been tested by Manovic et al. in TGA, fixed bed and a 75
KWth dual fluidized bed combustion plant.
[0006] Grace et al. have also investigated the pretreatment of
the sorbent by hydration at atmospheric pressure at 150[deg.] C.
and 300[deg.] C. From thermodynamics it is seen that complete
hydration does not occur spontaneously at temperature of
300[deg.] C. and hence complete reactivation of the sorbent is
not achieved by these methods. In addition, this method has also
been developed to be applied once in a few cycles and hence
sorbent degradation still occurs.
[0007] The reactivation of the sorbent by recarbonation has also
been investigated but this process requires an additional
calcination step which is very energy consuming and
uneconomical.
[0008] Zeeman et al. have integrated the hydration process as a
reactivation step in the CO2 removal process. They hydrate the
sorbent at 300[deg.] C. in the presence of CO2 and steam at
atmospheric pressure. There has been no mention about the extent
of hydration achieved by this process and the amount of
carbonation occurring during the hydration process. Although
this method was found to reduce sintering and reactivate the
sorbent a steady decline in the reactivity of the sorbent was
still observed.
[0009] Consequently, it can be understood that there is a need
for a cost effective and efficient system and method to minimize
the sintering of the selected sorbent and overcome the sorbents
decay in reactivity. Exemplary systems and methods of the
inventive concept satisfy these needs/preferences.
SUMMARY OF
THE INVENTIVE CONCEPT
[0010] Exemplary embodiments of the present invention are
directed to economically feasible options for the integration of
calcium sorbent based CO2 capture technology in post-combustion
systems, specifically in coal-fired power plants. Exemplary
embodiments described herein may also be applicable for
pre-combustion systems. Exemplary embodiments of the inventive
concept specifically provide process integration options while
factoring in such variables as location(s) of flue/fuel gas
drawn for CO2 capture, source of steam for the hydrator, solids
purge and recycle locations, particle capture devices (PCDs),
reactor configurations, heat management, and a variety of other
factors.
[0011] In contrast to the above mentioned methods of sorbent
reactivation. The Ohio State University has developed a process
to completely reactivate the sorbent in an energy efficient
manner using pressure hydration. The complete reactivation of
the sorbent during every cycle reverses the effect of sintering
and the history of the number of cycles is completely lost.
Hence, this process minimizes the amount of solids circulation
in the system. In addition, pressure hydration of the sorbent
may be conducted at high temperatures of 600[deg.] C. and the
exothermic energy of hydration is used to supply the endothermic
energy of dehydration. In addition, pressure hydration does not
require the cooling and reheating of the sorbent thereby
reducing the parasitic energy consumption of the process.
Extensive experiments have been conducted at the Ohio State
University wherein complete regeneration of the sorbent has been
observed for a number of cycles. Pressure hydration as used
herein does not require saturation pressure or high pressure of
operation. A pressure of above 6 bar is sufficient for a
temperature of 600[deg.] C. As the temperature decreases the
pressure required is also reduced. Thus, the hydration process
proposed by the Ohio state University is energy efficient and
economical.
[0012] Embodiments of the present invention detail a process for
the efficient capture of CO2 and sulfur from combustion flue gas
streams and gasification based fuel gas mixtures using
regenerable and recyclable calcium based sorbents. In exemplary
embodiments, the solid sorbent is predominantly a metal oxide
that can be converted into a hydrate. Some exemplary embodiments
specifically provide a method of reactivating the sorbent by
hydrating it at a high temperature of about 600[deg.] C. and a
pressure higher than about 6 bars in order to lower the
parasitic energy consumption of the process. In other exemplary
embodiments, hydration occurs at temperatures high enough such
that heat generated from exothermic reaction can be extracted to
generate steam for a steam turbine or used for heat exchange;
minimum of at least 300[deg.] C. and greater for steam turbine
integration. At higher hydration temperatures, greater than
about 500[deg.] C., process efficiency increases, but hydration
must operate at pressures greater than 1 atm. At temperatures
between about 300[deg.] C. to about 500[deg.] C. hydration may
occur at about 1 atmosphere. More specifically, temperature from
between 350[deg.] C. and about 512[deg.] C. By hydrating the
sorbent at high temperatures the energy loss due to solids
heating and cooling can be avoided and most crucially the
exothermic energy of hydration can be used to provide the energy
required for the dehydration of the sorbent or to generate high
quality steam for additional electricity generation. At high
temperatures of 600[deg.] C., the hydration reaction proceeds to
completion only at pressures higher than 6 bars and hence the
hydration is conducted at high pressures.
[0013] In other exemplary embodiments at different temperatures
of sorbent hydration, the pressure must also be adjusted to
maintain maximum reactivity. This reactivation procedure which
follows the calcination step during every carbonation
calcination cycle produces a high capacity regenerable sorbent
which aids in lowering the total amount of solids in circulation
making the CO2 capture process economically attractive...
CIRCULATING FLUIDIZED BED WITH MOVING BED DOWNCOMERS AND GAS
SEALING BETWEEN REACTORS
WO2012064712
[ PDF ]
A system and process
for carrying out one or more chemical reactions are provided and
include one or more chemical reactors having particulate solids
forming a bed therein, and a gas stripping zone forming a
non-mechanical seal between said reactors which includes a
conduit connecting the reactors. The conduit includes an inlet
for a stripping gas which is adapted to prevent process gas from
passing between reactors while permitting particulate solids to
pass between reactors.