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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a Range of Hydrogen Production Processes". Int. J. Hydrogen
Energy. 1998, 23, 653-659.
Roark, S. E.; Mackay, R.; Sammells, A. F. "Hydrogen Separation
Membranes for Vision 21 Energy Plants". Proceedings of the
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
Characteristics". Ind. Eng. Chem. Res. 1997, 36, 2141-2148.
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Formations-Coalbeds and Deep Saline Aquifers". J. Air & Waste
Manage. Assoc. 2003, 53, 645-715.
Wu, S.; Uddin, M. A.; Su, C.; Nagamine, S.; Sasaoka, E. "Effect of
Pore-Size Distribution of Lime on the Reactivity for the 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.