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| United States Patent Application |
20090165382
|
| Kind Code
|
A1
|
|
Rappas; Alkis S.
;   et al.
|
July 2, 2009
|
Catalytic Gasification Process with Recovery of Alkali Metal from Char
Abstract
Processes for extracting and recycling alkali metal compounds present in
the char produced from the catalytic gasification of carbonaceous
materials are provided involving at least contacting the char with and
alkali metal hydroxide followed by carbon dioxide. Both the alkali metal
hydroxide and carbon dioxide treatments serve to convert at least a
portion of the insoluble alkali metal compounds in the char into soluble
species which can be recovered and recycled.
| Inventors: |
Rappas; Alkis S.; (Kingwood, TX)
; Spitz; Robert A.; (Abington, MA)
|
| Correspondence Address:
|
MCDONNELL BOEHNEN HULBERT & BERGHOFF LLP
300 S. WACKER DRIVE, SUITE 3100
CHICAGO
IL
60606
US
|
| Assignee: |
GreatPoint Energy, Inc.
Chicago
IL
|
| Serial No.:
|
342715 |
| Series Code:
|
12
|
| Filed:
|
December 23, 2008 |
| Current U.S. Class: |
48/127.7; 48/210; 75/419; 75/742 |
| Class at Publication: |
48/127.7; 75/419; 75/742; 48/210 |
| International Class: |
C10J 3/00 20060101 C10J003/00; C22B 26/10 20060101 C22B026/10 |
Claims
1. A process for extracting and recovering alkali metal from a char, the
char comprising (i) one or more soluble alkali metal compounds and (ii)
insoluble matter comprising one or more insoluble alkali metal compounds,
the process comprising the steps of:(a) providing the char at an elevated
temperature ranging from 50.degree. C. to about 600.degree. C.;(b)
quenching the char in an aqueous medium to fracture the char and form a
quenched char slurry;(c) contacting the quenched char slurry with an
alkali metal hydroxide under suitable pressure and temperature so as to
convert at least a portion of the insoluble alkali metal compounds to one
or more soluble alkali metal compounds, and produce a first leached
slurry comprising the soluble alkali metal compounds and a partially
extracted insoluble matter;(d) contacting the first leached slurry with
carbon dioxide under suitable pressure and temperature so as to convert
at least a portion of the insoluble alkali metal compounds to one or more
soluble alkali metal compounds, and produce a second leached slurry
comprising the soluble alkali metal compounds and a residual insoluble
matter;(e) degassing the second leached slurry under suitable pressure
and temperature so as to remove a substantial portion of the excess
carbon dioxide and hydrogen sulfide, if present, and produce a degassed
second leached slurry;(f) separating the degassed second leached slurry
into a first liquid stream and a residual insoluble matter stream, the
first liquid stream comprising a predominant portion of the soluble
alkali metal compounds from the degassed second leached slurry, and the
residual insoluble matter stream comprising residual soluble alkali metal
compounds and residual insoluble alkali metal compounds;(g) recovering
the first liquid stream; and(h) washing the residual insoluble matter
stream with an aqueous medium to produce a first wash stream comprising
substantially all of the residual soluble alkali metal compounds from the
residual insoluble matter stream,wherein the quenching and contacting is
performed in the substantial absence of gaseous oxygen.
2. The process according to claim 1, wherein the char is a solid residue
derived from gasification of a carbonaceous material in the presence of
an alkali metal.
3. The process according to claim 2, wherein the carbonaceous material
comprises one or more of coal, petroleum coke, asphaltene, liquid
petroleum residue or biomass.
4. The process according to claim 1, wherein the aqueous medium to
fracture the char comprises the first wash stream.
5. The process according to claim 1, wherein the alkali metal comprises
sodium and/or potassium.
6. The process according to claim 2, wherein the alkali metal comprises
sodium and/or potassium.
7. The process according to claim 1, wherein the alkali metal is
potassium.
8. The process according to claim 1, wherein the source of alkali metal is
potassium carbonate.
9. The process according to claim 1, wherein contacting the quenched char
slurry with an alkali metal hydroxide is performed at a temperature
ranging from about 100.degree. C. up to about 300.degree. C., a steam
pressure ranging from about 25 up to about 1000 psig, and time ranging
from about 1 minute up to about 180 minutes.
10. A process for catalytically converting a carbonaceous composition, in
the presence of an alkali metal gasification catalyst, into a plurality
of gaseous products, the process comprising the steps of:(a) supplying a
carbonaceous composition to a gasification reactor, the carbonaceous
composition comprising ash;(b) reacting the carbonaceous composition in
the gasification reactor in the presence of steam and an alkali metal
gasification catalyst under suitable temperature and pressure to form (i)
a char comprising alkali metal from the alkali metal gasification
catalyst in the form of one or more soluble alkali metal compounds and
one or more insoluble alkali metal compounds, and (ii) a plurality of
gaseous products comprising methane and one or more of hydrogen, carbon
monoxide, carbon dioxide, hydrogen sulfide, ammonia, and other higher
hydrocarbons;(c) removing a portion of the char from the gasification
reactor;(d) extracting and recovering a substantial portion of the alkali
metal from the char according to the process of claim 1; and(e) at least
partially separating the plurality of gaseous products to produce a
stream comprising a predominant amount of one of the gaseous products.
11. The process according to claim 10, wherein the carbonaceous
composition comprises one or more of coal, petroleum coke, asphaltene,
liquid petroleum residue or biomass.
12. The process according to claim 10, wherein the stream comprises a
predominant amount of methane.
13. The process according to claim 10, wherein the alkali metal comprises
sodium and/or potassium.
Description
CROSS-REFERENCE TO RELATED APPLICATIONS
[0001]This application claims priority under 35 U.S.C. .sctn.119 from U.S.
Provisional Application Ser. No. 61/017,312 (filed Dec. 28, 2007), the
disclosure of which is incorporated by reference herein for all purposes
as if fully set forth.
[0002]This application is related to commonly owned U.S. application Ser.
No. 11/421,511, filed Jun. 1, 2006, entitled "CATALYTIC STEAM
GASIFICATION PROCESS WITH RECOVERY AND RECYCLE OF ALKALI METAL
COMPOUNDS"; U.S. application Ser. No. ______, (filed concurrently
herewith), entitled "CATALYTIC GASIFICATION PROCESS WITH RECOVERY OF
ALKALI METAL FROM CHAR" (attorney docket no. FN-0007 US NP1); U.S.
application Ser. No. ______, (filed concurrently herewith), entitled
"CATALYTIC GASIFICATION PROCESS WITH RECOVERY OF ALKALI METAL FROM CHAR"
(attorney docket no. FN-0015 US NP1); and U.S. application Ser. No.
______, (filed concurrently herewith), entitled "CATALYTIC GASIFICATION
PROCESS WITH RECOVERY OF ALKALI METAL FROM CHAR" (attorney docket no.
FN-0016 US NP1).
FIELD OF THE INVENTION
[0003]The present invention relates to a catalytic gasification process
that involves the extraction and recovery of alkali metal from char that
remains following catalytic gasification of a carbonaceous composition.
Further, the invention relates to processes for extracting and recovering
alkali metal from char by reacting a slurry of char particulate with
carbon dioxide under suitable temperature and pressure so as to convert
insoluble alkali metal compounds contained in the insoluble char
particulate to soluble alkali metal compounds.
BACKGROUND OF THE INVENTION
[0004]In view of numerous factors such as higher energy prices and
environmental concerns, the production of value-added gaseous products
from lower-fuel-value carbonaceous feedstocks, such as petroleum coke and
coal, is receiving renewed attention. The catalytic gasification of such
materials to produce methane and other value-added gases is disclosed,
for example, in U.S. Pat. No. 3,828,474, U.S. Pat. No. 3,998,607, U.S.
Pat. No. 4,057,512, U.S. Pat. No. 4,092,125, U.S. Pat. No. 4,094,650,
U.S. Pat. No. 4,204,843, U.S. Pat. No. 4,468,231, U.S. Pat. No.
4,500,323, U.S. Pat. No. 4,541,841, U.S. Pat. No. 4,551,155, U.S. Pat.
No. 4,558,027, U.S. Pat. No. 4,606,105, U.S. Pat. No. 4,617,027, U.S.
Pat. No. 4,609,456, U.S. Pat. No. 5,017,282, U.S. Pat. No. 5,055,181,
U.S. Pat. No. 6,187,465, U.S. Pat. No. 6,790,430, U.S. Pat. No.
6,894,183, U.S. Pat. No. 6,955,695, US2003/0167961A1, US2006/0265953A1,
US2007/000177A1, US2007/083072A1, US2007/0277437A1 and GB 1599932.
[0005]Gasification of a carbonaceous material, such as coal or petroleum
coke, can be catalyzed by loading the carbonaceous material with a
catalyst comprising an alkali metal source. US2007/0000177A1 and
US2007/0083072A1, both incorporated herein by reference, disclose the
alkali-metal-catalyzed gasification of carbonaceous materials.
Lower-fuel-value carbon sources, such as coal, typically contain
quantities of inorganic matter, including compounds of silicon, aluminum,
calcium, iron, vanadium, sulfur, and the like. This inorganic content is
referred to as ash. Silica and alumina are especially common ash
components. At temperatures above 500-600.degree. C., alkali metal
compounds can react with the alumina and silica to form alkali metal
aluminosilicates. As an aluminosilicate, the alkali metal compound is
substantially insoluble in water and has little effectiveness as a
gasification catalyst.
[0006]At typical gasification temperatures, most components of ash are not
gasified, and thus build up with other compounds in the gasification
reactor as a solid residue referred to as char. For catalytic
gasification, char generally includes ash, unconverted carbonaceous
material, and alkali metal compounds (from the catalyst). The char must
be periodically withdrawn from the reactor through a solid purge. The
char may contain substantial quantities of alkali metal compounds. The
alkali metal compounds may exist in the char as soluble species, such as
potassium carbonate, but may also exist as insoluble species, such as
potassium aluminosilicate (e.g., kaliophilite). It is desirable to
recover the soluble and the insoluble alkali metal compounds from the
solid purge for subsequent reuse as a gasification catalyst. A need
remains for efficient processes for recovering soluble and insoluble
alkali metal compounds from char. Such processes should effect
substantial recovery of alkali metal compounds from the char, minimize
the complexity of the processing steps, reduce the use of consumable raw
materials, and generate few waste products that require disposal.
SUMMARY OF THE INVENTION
[0007]The present invention provides processes for converting a
carbonaceous composition into a plurality of gaseous products with
recovery of an alkali metal compounds that can be reused as a
gasification catalyst. The invention further provides processes for
extracting and recovering catalytically useful alkali metal compounds
from soluble and insoluble alkali metal compounds contained in char,
where the processes involve thermal quenching of the char in an aqueous
medium followed by treatment of the char particulate with carbon dioxide
gas under hydrothermal conditions.
[0008]In a first aspect, the invention provides a process for extracting
and recovering alkali metal from a char, the char comprising (i) one or
more soluble alkali metal compounds and (ii) insoluble matter comprising
one or more insoluble alkali metal compounds, the process comprising the
steps of: (a) providing the char at an elevated temperature ranging from
50.degree. C. to about 600.degree. C.; (b) quenching the char in an
aqueous medium to fracture the char and form a quenched char slurry; (c)
contacting the quenched char slurry with an alkali metal hydroxide under
suitable pressure and temperature so as to convert at least a portion of
the insoluble alkali metal compounds to one or more soluble alkali metal
compounds, and produce a first leached slurry comprising the soluble
alkali metal compounds and residual insoluble matter; (d) contacting the
first leached slurry with carbon dioxide under suitable pressure and
temperature so as to convert at least a portion of the insoluble alkali
metal compounds to one or more soluble alkali metal compounds, and
produce a second leached slurry comprising the soluble alkali metal
compounds and residual insoluble matter; (e) degassing the second leached
slurry under suitable pressure and temperature so as to remove a
substantial portion of the excess carbon dioxide and hydrogen sulfide, if
present, and produce a degassed second leached slurry; (f) separating the
degassed second leached slurry into a first liquid stream and a residual
insoluble matter stream, the first liquid stream comprising a predominant
portion of the soluble alkali metal compounds from the degassed second
leached slurry, and the residual insoluble matter stream comprising
residual soluble alkali metal compounds and residual insoluble alkali
metal compounds; (g) recovering the first liquid stream; and (h) washing
the residual insoluble matter stream with an aqueous medium to produce a
first wash stream comprising substantially all of the residual soluble
alkali metal compounds from the residual insoluble matter stream, wherein
the quenching and contacting is performed in the substantial absence of
gaseous oxygen.
[0009]In a second aspect, the invention provides a process for
catalytically converting a carbonaceous composition, in the presence of
an alkali metal gasification catalyst, into a plurality of gaseous
products, the process comprising the steps of: (a) supplying a
carbonaceous composition to a gasification reactor, the carbonaceous
composition comprising an ash; (b) reacting the carbonaceous composition
in the gasification reactor in the presence of steam and an alkali metal
gasification catalyst under suitable temperature and pressure to form (i)
a char comprising alkali metal from the alkali metal gasification
catalyst in the form of one or more soluble alkali metal compounds and
one or more insoluble alkali metal compounds, and (ii) a plurality of
gaseous products comprising methane and one or more of hydrogen, carbon
monoxide, carbon dioxide, hydrogen sulfide, ammonia, and other higher
hydrocarbons; (c) removing a portion of the char from the gasification
reactor; (d) extracting and recovering a substantial portion of the
alkali metal from the char according to any process of the first aspect
of the invention; and (e) at least partially separating the plurality of
gaseous products to produce a stream comprising a predominant amount of
one of the gaseous products.
[0010]The process can be run continuously, and the recovered alkali metal
can be recycled back into the process to minimize the amount of makeup
catalyst required.
BRIEF DESCRIPTION OF THE DRAWINGS
[0011]FIG. 1 provides a schematic diagram for one example of a process for
recovering alkali metal from char for reuse as a catalyst in a catalytic
gasification process.
DETAILED DESCRIPTION
[0012]The present invention relates to processes for the catalytic
conversion of a carbonaceous composition into a plurality of gaseous
products with substantial recovery of alkali metal used as the
gasification catalyst. The alkali metal is recovered from char that
develops as a result of the catalyzed gasification of a carbonaceous
material in a gasification reactor. The alkali metal may exist in the
char in either water-soluble or water-insoluble forms. The present
invention provides efficient processes for extracting and recovering
substantially all of the soluble and insoluble alkali metal from char.
Among other steps, these processes include the quenching of the char in
an aqueous solution to fracture the char, dissolving substantially all of
the water-soluble alkali metal compounds, and forming a slurry of the
quenched char, and the reacting of a char slurry with an alkali metal
hydroxide followed by carbon dioxide at suitable pressures and
temperatures to solubilize and extract insoluble alkali metal compounds.
In this manner, soluble and insoluble alkali metal compounds are
substantially removed from char using simplified processes that require
few consumable raw materials.
[0013]The present invention can be practiced, for example, using any of
the developments to catalytic gasification technology disclosed in
commonly owned US2007/0000177A1, US2007/0083072A1 and US2007/0277437A1;
and U.S. patent application Ser. No. 12/178,380 (filed 23 Jul. 2008),
Ser. No. 12/234,012 (filed 19 Sep. 2008) and Ser. No. 12/234,018 (filed
19 Sep. 2008). Moreover, the present invention can be practiced using
developments described in the following U.S. Patent Applications, each of
which was filed on even date herewith and is hereby incorporated herein
by reference: Ser. No. ______, entitled "PETROLEUM COKE COMPOSITIONS FOR
CATALYTIC GASIFICATION" (attorney docket no. FN-0008 US NP1); Ser. No.
______, entitled "STEAM GENERATING SLURRY GASIFIER FOR THE CATALYTIC
GASIFICATION OF A CARBONACEOUS FEEDSTOCK" (attorney docket no. FN-0017 US
NP1); Ser. No. ______, entitled "PETROLEUM COKE COMPOSITIONS FOR
CATALYTIC GASIFICATION" (attorney docket no. FN-0011 US NP 1); Ser. No.
______, entitled "COAL COMPOSITIONS FOR CATALYTIC GASIFICATION" (attorney
docket no. FN-0009 US NP1); Ser. No. ______, entitled "PROCESSES FOR
MAKING SYNTHESIS GAS AND SYNGAS-DERIVED PRODUCTS" (attorney docket no.
FN-0010 US NP1); Ser. No. ______, entitled "CARBONACEOUS FUELS AND
PROCESSES FOR MAKING AND USING THEM" (attorney docket no. FN-0013 US
NP1); and Ser. No. ______, entitled "PROCESSES FOR MAKING SYNGAS-DERIVED
PRODUCTS" (attorney docket no. FN-0012 US NP1).
[0014]All publications, patent applications, patents and other references
mentioned herein, if not otherwise indicated, are explicitly incorporated
by reference herein in their entirety for all purposes as if fully set
forth.
[0015]Unless otherwise defined, all technical and scientific terms used
herein have the same meaning as commonly understood by one of ordinary
skill in the art to which this disclosure belongs. In case of conflict,
the present specification, including definitions, will control.
[0016]Except where expressly noted, trademarks are shown in upper case.
[0017]Although methods and materials similar or equivalent to those
described herein can be used in the practice or testing of the present
disclosure, suitable methods and materials are described herein.
[0018]Unless stated otherwise, all percentages, parts, ratios, etc., are
by weight.
[0019]When an amount, concentration, or other value or parameter is given
as a range, or a list of upper and lower values, this is to be understood
as specifically disclosing all ranges formed from any pair of any upper
and lower range limits, regardless of whether ranges are separately
disclosed. Where a range of numerical values is recited herein, unless
otherwise stated, the range is intended to include the endpoints thereof,
and all integers and fractions within the range. It is not intended that
the scope of the present disclosure be limited to the specific values
recited when defining a range.
[0020]When the term "about" is used in describing a value or an end-point
of a range, the disclosure should be understood to include the specific
value or end-point referred to.
[0021]As used herein, the terms "comprises," "comprising," "includes,"
"including," "has," "having" or any other variation thereof, are intended
to cover a non-exclusive inclusion. For example, a process, method,
article, or apparatus that comprises a list of elements is not
necessarily limited to only those elements but can include other elements
not expressly listed or inherent to such process, method, article, or
apparatus. Further, unless expressly stated to the contrary, "or" refers
to an inclusive or and not to an exclusive or. For example, a condition A
or B is satisfied by any one of the following: A is true (or present) and
B is false (or not present), A is false (or not present) and B is true
(or present), and both A and B are true (or present).
[0022]The use of "a" or "an" to describe the various elements and
components herein is merely for convenience and to give a general sense
of the disclosure. This description should be read to include one or at
least one and the singular also includes the plural unless it is obvious
that it is meant otherwise.
[0023]The materials, methods, and examples herein are illustrative only
and, except as specifically stated, are not intended to be limiting.
Carbonaceous Composition
[0024]The term "carbonaceous material" or "carbonaceous composition" as
used herein includes a carbon source, typically coal, petroleum coke,
asphaltene and/or liquid petroleum residue, but may broadly include any
source of carbon suitable for gasification, including biomass. The
carbonaceous composition will generally include at least some ash,
typically at least about 3 wt % ash (based on the weight of the
carbonaceous composition).
[0025]The term "petroleum coke" as used herein includes both (i) the solid
thermal decomposition product of high-boiling hydrocarbon fractions
obtained in petroleum processing (heavy residues--"resid petcoke") and
(ii) the solid thermal decomposition product of processing tar sands
(bituminous sands or oil sands--"tar sands petcoke"). Such carbonization
products include, for example, green, calcined, needle and fluidized bed
petroleum coke.
[0026]Resid petcoke can be derived from a crude oil, for example, by
coking processes used for upgrading heavy-gravity residual crude oil,
which petroleum coke contains ash as a minor component, typically about
1.0 wt % or less, and more typically about 0.5 wt % of less, based on the
weight of the coke. Typically, the ash in such lower-ash cokes
predominantly comprises metals such as nickel and vanadium.
[0027]Tar sands petcoke can be derived from an oil sand, for example, by
coking processes used for upgrading oil sand. Tar sands petcoke contains
ash as a minor component, typically in the range of about 2 wt % to about
12 wt %, and more typically in the range of about 4 wt % to about 12 wt
%, based on the overall weight of the tar sands petcoke. Typically, the
ash in such higher-ash cokes predominantly comprises materials such as
compounds of silicon and/or aluminum.
[0028]The petroleum coke can comprise at least about 70 wt % carbon, at
least about 80 wt % carbon, or at least about 90 wt % carbon, based on
the total weight of the petroleum coke. Typically, the petroleum coke
comprises less than about 20 wt % percent inorganic compounds, based on
the weight of the petroleum coke.
[0029]The term "asphaltene" as used herein is an aromatic carbonaceous
solid at room temperature, and can be derived, from example, from the
processing of crude oil and crude oil tar sands.
[0030]The term "liquid petroleum residue" as used herein includes both (i)
the liquid thermal decomposition product of high-boiling hydrocarbon
fractions obtained in petroleum processing (heavy residues--"resid liquid
petroleum residue") and (ii) the liquid thermal decomposition product of
processing tar sands (bituminous sands or oil sands--"tar sands liquid
petroleum residue"). The liquid petroleum residue is substantially
non-solid; for example, it can take the form of a thick fluid or a
sludge.
[0031]Resid liquid petroleum residue can be derived from a crude oil, for
example, by processes used for upgrading heavy-gravity crude oil
distillation residue. Such liquid petroleum residue contains ash as a
minor component, typically about 1.0 wt % or less, and more typically
about 0.5 wt % of less, based on the weight of the residue. Typically,
the ash in such lower-ash residues predominantly comprises metals such as
nickel and vanadium.
[0032]Tar sands liquid petroleum residue can be derived from an oil sand,
for example, by processes used for upgrading oil sand. Tar sands liquid
petroleum residue contains ash as a minor component, typically in the
range of about 2 wt % to about 12 wt %, and more typically in the range
of about 4 wt % to about 12 wt %, based on the overall weight of the
residue. Typically, the ash in such higher-ash residues predominantly
comprises materials such as compounds of silicon and/or aluminum.
[0033]The term "coal" as used herein means peat, lignite, sub-bituminous
coal, bituminous coal, anthracite, or mixtures thereof. In certain
embodiments, the coal has a carbon content of less than about 85%, or
less than about 80%, or less than about 75%, or less than about 70%, or
less than about 65%, or less than about 60%, or less than about 55%, or
less than about 50% by weight, based on the total coal weight. In other
embodiments, the coal has a carbon content ranging up to about 85%, or up
to about 80%, or up to about 75% by weight, based on total coal weight.
Examples of useful coals include, but are not limited to, Illinois #6,
Pittsburgh #8, Beulah (N.D.), Utah Blind Canyon, and Powder River Basin
(PRB) coals. Anthracite, bituminous coal, sub-bituminous coal, and
lignite coal may contain about 10 wt %, from about 5 to about 7 wt %,
from about 4 to about 8 wt %, and from about 9 to about 11 wt %, ash by
total weight of the coal on a dry basis, respectively. However, the ash
content of any particular coal source will depend on the rank and source
of the coal, as is familiar to those skilled in the art. See, for
example, "Coal Data: A Reference", Energy Information Administration,
Office of Coal, Nuclear, Electric and Alternate Fuels, U.S. Department of
Energy, DOE/EIA-0064(93), February 1995.
[0034]The term "ash" as used herein includes inorganic compounds that
occur within the carbon source. The ash typically includes compounds of
silicon, aluminum, calcium, iron, vanadium, sulfur, and the like. Such
compounds include inorganic oxides, such as silica, alumina, ferric
oxide, etc., but may also include a variety of minerals containing one or
more of silicon, aluminum, calcium, iron, and vanadium. The term "ash"
may be used to refer to such compounds present in the carbon source prior
to gasification, and may also be used to refer to such compounds present
in the char after gasification.
Alkali Metal Compounds
[0035]As used herein, the terms "alkali metal compound" refers to a free
alkali metal, as a neutral atom or ion, or to a molecular entity, such as
a salt, that contains an alkali metal. Additionally, the term "alkali
metal" may refer either to an individual alkali metal compound, as
heretofore defined, or may also refer to a plurality of such alkali metal
compounds. An alkali metal compound capable of being substantially
solubilized by water is referred to as a "soluble alkali metal compound."
Examples of a soluble alkali metal compound include free alkali metal
cations and water-soluble alkali metal salts, such as potassium
carbonate, potassium hydroxide, and the like. An alkali metal compound
incapable of being substantially solubilized by water is referred to as
an "insoluble alkali metal compound." Examples of an insoluble alkali
metal compound include water-insoluble alkali metal salts and/or
molecular entities, such as potassium aluminosilicate.
[0036]Alkali metal compounds suitable for use as a gasification catalyst
include compounds selected from the group consisting of alkali metal
carbonates, bicarbonates, formates, oxalates, amides, hydroxides,
acetates, halides, nitrates, sulfides, and polysulfides. For example, the
catalyst can comprise one or more of Na.sub.2CO.sub.3, K.sub.2CO.sub.3,
Rb.sub.2CO.sub.3, Li.sub.2CO.sub.3, Cs.sub.2CO.sub.3, NaOh, KOH, RbOH, or
CsOH, and particularly, potassium carbonate and/or potassium hydroxide.
Catalyst-Loaded Carbonaceous Feedstock
[0037]The carbonaceous composition is generally loaded with an amount of
an alkali metal. Typically, the quantity of the alkali metal in the
composition is sufficient to provide a ratio of alkali metal atoms to
carbon atoms ranging from about 0.01, or from about 0.02, or from about
0.03, or from about 0.04, to about 0.06, or to about 0.07, or to about
0.08. Further, the alkali metal is typically loaded onto a carbon source
to achieve an alkali metal content of from about 3 to about 10 times more
than the combined ash content of the carbonaceous material (e.g., coal
and/or petroleum coke), on a mass basis.
[0038]Any methods known to those skilled in the art can be used to
associate one or more gasification catalysts with the carbonaceous
composition. Such methods include, but are not limited to, admixing with
a solid catalyst source and impregnating the catalyst onto the
carbonaceous solid. Several impregnation methods known to those skilled
in the art can be employed to incorporate the gasification catalysts.
These methods include, but are not limited to, incipient wetness
impregnation, evaporative impregnation, vacuum impregnation, dip
impregnation, and combinations of these methods. Gasification catalysts
can be impregnated into the carbonaceous solids by slurrying with a
solution (e.g., aqueous) of the catalyst.
[0039]That portion of the carbonaceous feedstock of a particle size
suitable for use in the gasifying reactor can then be further processed,
for example, to impregnate one or more catalysts and/or cocatalysts by
methods known in the art, for example, as disclosed in U.S. Pat. No.
4,069,304 and U.S. Pat. No. 5,435,940; previously incorporated U.S. Pat.
No. 4,092,125, U.S. Pat. No. 4,468,231 and U.S. Pat. No. 4,551,155;
previously incorporated U.S. patent application Ser. Nos. 12/234,012 and
12/234,018; and previously incorporated U.S. patent applications Ser. No.
______, entitled "PETROLEUM COKE COMPOSITIONS FOR CATALYTIC GASIFICATION"
(attorney docket no. FN-0008 US NP1), Ser. No. ______, entitled
"PETROLEUM COKE COMPOSITIONS FOR CATALYTIC GASIFICATION" (attorney docket
no. FN-0011 US NP1), Ser. No. ______, entitled "CONTINUOUS PROCESS FOR
CONVERTING CARBONACEOUS FEEDSTOCK INTO GASEOUS PRODUCTS" (attorney docket
no. FN-0018 US NP1), and Ser. No. ______, entitled "COAL COMPOSITIONS FOR
CATALYTIC GASIFICATION" (attorney docket no. FN-0009 US NP1).
[0040]One particular method suitable for combining the coal particulate
with a gasification catalyst to provide a catalyzed carbonaceous
feedstock where the catalyst has been associated with the coal
particulate via ion exchange is described in previously incorporated U.S.
patent application Ser. No. 12/178,380 (filed 23 Jul. 2008). The catalyst
loading by ion exchange mechanism is maximized (based on adsorption
isotherms specifically developed for the coal), and the additional
catalyst retained on the wet cake, including inside the pores, is
controlled so that the total catalyst target value is obtained in a
controlled manner. Such loading provides a catalyzed coal particulate as
a wet cake. The catalyst loaded and dewatered wet coal cake typically
contains, for example, about 50% moisture. The total amount of catalyst
loaded is controlled by controlling the concentration of catalyst
components in the solution, as well as the contact time, temperature and
method, as can be readily determined by those of ordinary skill in the
relevant art based on the characteristics of the starting coal.
[0041]The catalyzed feedstock can be stored for future use or transferred
to a feed operation for introduction into the gasification reactor. The
catalyzed feedstock can be conveyed to storage or feed operations
according to any methods known to those skilled in the art, for example,
a screw conveyer or pneumatic transport.
Catalytic Gasification Methods
[0042]The extraction and recovery methods of the present invention are
particularly useful in integrated gasification processes for converting
carbonaceous feedstocks, such as petroleum coke, liquid petroleum residue
and/or coal, to combustible gases, such as methane. The gasification
reactors for such processes are typically operated at moderately high
pressures and temperature, requiring introduction of a carbonaceous
material (i.e. a feedstock) to the reaction zone of the gasification
reactor while maintaining the required temperature, pressure, and flow
rate of the feedstock. Those skilled in the art are familiar with feed
systems for providing feedstocks to high pressure and/or temperature
environments, including, star feeders, screw feeders, rotary pistons, and
lock-hoppers. It should be understood that the feed system can include
two or more pressure-balanced elements, such as lock hoppers, which would
be used alternately.
[0043]Suitable gasification reactors include counter-current fixed bed,
co-current fixed bed, fluidized bed, entrained flow, and moving bed
reactors. The gasification reactor typically will be operated at moderate
temperatures of at least about 450.degree. C., or of at least about
600.degree. C. or above, to about 900.degree. C., or to about 750.degree.
C., or to about 700.degree. C.; and at pressures of at least about 50
psig, or at least about 200 psig, or at least about 400 psig, to about
1000 psig, or to about 700 psig, or to about 600 psig.
[0044]The gas utilized in the gasification reactor for pressurization and
reactions of the particulate composition typically comprises steam, and
optionally, oxygen or air, and are supplied to the reactor according to
methods known to those skilled in the art. For example, any of the steam
boilers known to those skilled in the art can supply steam to the
reactor. Such boilers can be powered, for example, through the use of any
carbonaceous material such as powdered coal, biomass etc., and including
but not limited to rejected carbonaceous materials from the particulate
composition preparation operation (e.g., fines, supra). Steam can also be
supplied from a second gasification reactor coupled to a combustion
turbine where the exhaust from the reactor is thermally exchanged to a
water source and produce steam.
[0045]Recycled steam from other process operations can also be used for
supplying steam to the reactor. For example, when the slurried
particulate composition is dried with a fluid bed slurry drier, as
discussed previously, the steam generated through vaporization can be fed
to the gasification reactor.
[0046]The small amount of required heat input for the catalytic coal
gasification reaction can be provided by superheating a gas mixture of
steam and recycle gas feeding the gasification reactor by any method
known to one skilled in the art. In one method, compressed recycle gas of
CO and H.sub.2 can be mixed with steam and the resulting steam/recycle
gas mixture can be further superheated by heat exchange with the
gasification reactor effluent followed by superheating in a recycle gas
furnace.
[0047]A methane reformer can be included in the process to supplement the
recycle CO and H.sub.2 fed to the reactor to ensure that the reaction is
run under thermally neutral (adiabatic) conditions. In such instances,
methane can be supplied for the reformer from the methane product, as
described below.
[0048]Reaction of the particulate composition under the described
conditions typically provides a crude product gas and a char. The char
produced in the gasification reactor during the present processes
typically is removed from the gasification reactor for sampling, purging,
and/or catalyst recovery. Methods for removing char are well known to
those skilled in the art. One such method taught by EP-A-0102828, for
example, can be employed. The char can be periodically withdrawn from the
gasification reactor through a lock hopper system, although other methods
are known to those skilled in the art.
[0049]Crude product gas effluent leaving the gasification reactor can pass
through a portion of the gasification reactor which serves as a
disengagement zone where particles too heavy to be entrained by the gas
leaving the gasification reactor (i.e., fines) are returned to the
fluidized bed. The disengagement zone can include one or more internal
cyclone separators or similar devices for removing fines and particulates
from the gas. The gas effluent passing through the disengagement zone and
leaving the gasification reactor generally contains CH.sub.4, CO.sub.2,
H.sub.2 and CO, H.sub.2S, NH.sub.3, unreacted steam, entrained fines, and
other contaminants such as COS.
[0050]The gas stream from which the fines have been removed can then be
passed through a heat exchanger to cool the gas and the recovered heat
can be used to preheat recycle gas and generate high pressure steam.
Residual entrained fines can also be removed by any suitable means such
as external cyclone separators followed by Venturi scrubbers. The
recovered fines can be processed to recover alkali metal catalyst.
[0051]The gas stream exiting the Venturi scrubbers can be fed to COS
hydrolysis reactors for COS removal (sour process) and further cooled in
a heat exchanger to recover residual heat prior to entering water
scrubbers for ammonia recovery, yielding a scrubbed gas comprising at
least H.sub.2S, CO.sub.2, CO, H.sub.2 and CH.sub.4. Methods for COS
hydrolysis are known to those skilled in the art, for example, see U.S.
Pat. No. 4,100,256.
[0052]The residual heat from the scrubbed gas can be used to generate low
pressure steam. Scrubber water and sour process condensate can be
processed to strip and recover H.sub.2S, CO.sub.2 and NH.sub.3; such
processes are well known to those skilled in the art. NH.sub.3 can
typically be recovered as an aqueous solution (e.g., 20 wt %).
[0053]A subsequent acid gas removal process can be used to remove H.sub.2S
and CO.sub.2 from the scrubbed gas stream by a physical absorption method
involving solvent treatment of the gas to give a cleaned gas stream. Such
processes involve contacting the scrubbed gas with a solvent such as
monoethanolamine, diethanolamine, methyldiethanolamine, diisopropylamine,
diglycolamine, a solution of sodium salts of amino acids, methanol,
hot
potassium carbonate or the like. One method can involve the use of
Selexol.RTM. (UOP LLC, Des Plaines, Ill. USA) or Rectisol.RTM. (Lurgi AG,
Frankfurt am Main, Germany) solvent having two trains; each train
consisting of an H.sub.2S absorber and a CO.sub.2 absorber. The spent
solvent containing H.sub.2S, CO.sub.2 and other contaminants can be
regenerated by any method known to those skilled in the art, including
contacting the spent solvent with steam or other stripping gas to remove
the contaminants or by passing the spent solvent through stripper
columns. Recovered acid gases can be sent for sulfur recovery processing.
The resulting cleaned gas stream contains mostly CH.sub.4, H.sub.2 and CO
and, typically, small amounts of CO.sub.2 and H.sub.2O. Any recovered
H.sub.2S from the acid gas removal and sour water stripping can be
converted to elemental sulfur by any method known to those skilled in the
art, including the Claus process. Sulfur can be recovered as a molten
liquid.
[0054]The cleaned gas stream can be further processed to separate and
recover CH.sub.4 by any suitable gas separation method known to those
skilled in the art including, but not limited to, cryogenic distillation
and the use of molecular sieves or ceramic membranes. One method for
recovering CH.sub.4 from the cleaned gas stream involves the combined use
of molecular sieve absorbers to remove residual H.sub.2O and CO.sub.2 and
cryogenic distillation to fractionate and recover CH.sub.4. Typically,
two gas streams can be produced by the gas separation process, a methane
product stream and a syngas stream (H.sub.2 and CO). The syngas stream
can be compressed and recycled to the gasification reactor. If necessary,
a portion of the methane product can be directed to a reformer, as
discussed previously and/or a portion of the methane product can be used
as plant fuel.
Char
[0055]The term "char" as used herein includes mineral ash, unconverted
carbonaceous material, and water-soluble alkali metal compounds and
water-insoluble alkali metal compounds within the other solids. The char
produced in the gasification reactor typically is removed from the
gasification reactor for sampling, purging, and/or catalyst recovery.
Methods for removing char are well known to those skilled in the art. One
such method, described in previously incorporated EP-A-0102828, for
example, can be employed. The char can be periodically withdrawn from the
gasification reactor through a lock hopper system, although other methods
are known to those skilled in the art.
Catalyst Recovery
[0056]Alkali metal salts, particularly sodium and potassium salts, are
useful as catalysts in catalytic coal gasification reactions. Alkali
metal catalyst-loaded carbonaceous mixtures are generally prepared and
then introduced into a gasification reactor, or can be formed in situ by
introducing alkali metal catalyst and carbonaceous particles separately
into the reactor.
[0057]After gasification, the alkali metal may exist in the char as
species that are either soluble or insoluble. In particular, alkali metal
can react with mineral ash at temperatures above about 500-600.degree. C.
to form insoluble alkali metal aluminosilicates, such as kaliophilite. As
an aluminosilicate, or other insoluble compounds, the alkali metal is
ineffective as a catalyst.
[0058]As discussed, supra, char is periodically removed from the
gasification reactor through a solid purge. Because the char has a
substantial quantity of soluble and insoluble alkali metal, it is
desirable to recover the alkali metal from the char for reuse as a
gasification catalyst. Catalyst loss in the solid purge must generally be
compensated for by a reintroduction of additional catalyst, i.e., a
catalyst make-up stream. Processes have been developed to recover alkali
metal from the solid purge in order to reduce raw material costs and to
minimize environmental impact of a catalytic gasification process. For
example, a recovery and recycling process is described in previously
incorporated US2007/0277437A1.
[0059]The present invention provides a novel process for extracting and
recovering soluble and insoluble alkali metal from char.
1. Char Quenching (100)
[0060]Referring to FIG. 1, a char (10) removed from a gasification reactor
can be quenched in an aqueous medium (15) by any suitable means known to
those of skill in the art to fracture the char and form a quenched char
slurry (20) where the quenched char slurry comprising soluble alkali
metal compounds and insoluble matter comprising insoluble alkali metal
compounds. One particularly useful quenching method is described in
previously incorporated US2007/0277437A1.
[0061]The invention places no particular limits on the ratio of aqueous
medium to char, or on the temperature of the aqueous medium. In some
embodiments, however, the wt/wt ratio of water in the aqueous medium to
the water-insoluble component of the char ranges from about 3:1, or from
about 5:1, up to about 7:1, or up to about 15:1. Additionally, in some
embodiments, the aqueous medium has a temperature that ranges from about
95.degree. C. up to about 110.degree. C., or up to about 140.degree. C.,
or up to about 200.degree. C., or up to about 300.degree. C. The pressure
need not be elevated above atmospheric pressure. In some embodiments,
however, the quenching occurs at pressures higher than atmospheric
pressure. For example, the quenching may occur at pressures up to about
25 psig, or up to about 40 psig, or up to about 60 psig, or up to about
80 psig, or up to about 400 psig (including the partial pressure of
CO.sub.2). The quenching process preferably occurs under a stream of gas
that is substantially free of oxygen or other oxidants and comprises
carbon dioxide.
[0062]The quenching step fractures the heated char by dissolving the
rather large amount of water soluble alkali metal compounds (e.g.,
carbonates) that holds it together such that a quenched char slurry
results. The char leaves the gasification reactor at high temperature,
and it is typically cooled down. For example, the temperature of the char
may range from about 35.degree. C., or from about 50.degree. C., or from
about 75.degree. C., up to about 200.degree. C., or up to about
300.degree. C., or up to about 400.degree. C. In some embodiments, the
char has an elevated temperature ranging from about 50.degree. C. to
about 600.degree. C. The quenched char slurry comprises both soluble
alkali metal and insoluble alkali metal. As the char fractures, soluble
alkali metal leaches into the aqueous solution.
[0063]The char quenching is preferably performed in the substantial
absence of gaseous oxygen. For example, the leaching environment has less
than about 1% gaseous oxygen, or less than about 0.5% gaseous oxygen,
less than about 0.1% gaseous oxygen, less than about 0.01% gaseous
oxygen, or less than about 0.005% gaseous oxygen, based on the total
volume.
[0064]In some embodiments, the aqueous medium used in the quenching may
comprise a wash stream that results from a washing step of the present
invention, described, infra.
2. Contacting of Quenched Char Slurry with an Alkali Metal Hydroxide (200)
[0065]The quenched char slurry (20) can be contacted with an alkali metal
hydroxide (25) under suitable pressure and temperature so as to convert
at least a portion of the insoluble alkali metal compounds in the
insoluble matter to one or more soluble alkali metal compounds and
produce a first leached slurry (30) comprising soluble alkali metal
compounds and a partially extracted insoluble matter comprising insoluble
alkali metal compounds.
[0066]The contacting of the quenched char slurry (20) with the alkali
metal hydroxide (25) typically involves contacting the slurry at an
elevated temperature with an aqueous solution of the alkali metal
hydroxide such that at least a portion of the alkali metal from the
insoluble matter is extracted. Generally, the alkali metal hydroxide is
provided to the quenched char slurry (20) as an aqueous solution having a
concentration ranging form about 1 to about 10 M alkali metal hydroxide.
The alkali metal hydroxide can comprise any of LiOH, NaOH, KOH, RbOH, and
CsOH, as well as mixtures thereof, preferably, the alkali metal comprises
NaOH or KOH. Most preferably the alkali metal hydroxide comprises KOH.
[0067]The quenched char slurry can be pressurized and heated by the
introduction of heated and pressurized steam. For example, the
temperature of the slurry can range from about 100.degree. C., or from
about 125.degree. C., or from about 150.degree. C., up to about
240.degree. C., up to about 270.degree. C., or up to about 300.degree. C.
In some embodiments, the slurry has an elevated temperature ranging from
about 150.degree. C. to about 240.degree. C. In some embodiments, the
slurry has an elevated temperature ranging from about 100.degree. C. to
about 150.degree. C.
[0068]In any combination with the preceding temperature ranges, the slurry
can be maintained at a pressure of from about 25 psig, or from about 35
psig, or from about 50 psig, up to about 250 psig, or up to 500 psig, or
up to about 750 psig, or up to 1000 psig. In some embodiments, the slurry
may be maintained at a pressure of from about 50 to 500 psig. In other
embodiments, the slurry may be maintained at a pressure of from about 50
to 250 psig.
[0069]The slurry can be maintained at an appropriate temperature and
pressure for a residence time ranging from about 1 minute, or about 5
minutes, or about 15 minutes, or about 30 minutes, up to about 60
minutes, or up to about 120 minutes, or up to about 150 minutes, or up to
about 180 minutes. In some embodiments, the slurry may be maintained at
an appropriate temperature and pressure for a residence time ranging from
30 minutes to 150 minutes.
[0070]In one embodiment, the contacting takes place in a pressurized
leaching operation using at least 2, and preferably 3, continuous
stirred-tank reactors (CSTRs), either in series (e.g., co-current), or a
single horizontal pressure vessel with internal weirs and stirrers to
provide 3-6 internal stages for the slurry (the gas phase may optionally
be separated by stages).
3. Contacting of Quenched Char Slurry with Carbon Dioxide (300)
[0071]The contacting of the first leached slurry (30) with carbon dioxide
(35) occurs under pressure and temperature suitable to convert at least a
portion at least a portion, or even a predominant portion, of the
insoluble alkali metal compounds to one or more soluble alkali metal
compounds, and produce a second leached slurry comprising the soluble
alkali metal compounds and a residual insoluble matter. In the
alternative, this process step is referred to as a first leaching or a
first hydrothermal leaching.
[0072]In some instances, as can be determined by one skilled in the art,
prior to contacting the first leached slurry with carbon dioxide, the
temperature and/or pressure of the first leached slurry (30) can be
reduced according to those methods known to those skilled in the art. For
example, the first leached slurry can be flashed into a flash drum. Water
can also be evaporated from the first leached slurry (30) to increase the
concentration of alkali metals in the slurry solution. In one embodiment,
the first leached slurry may be cooled to a temperature ranging from
about 120.degree. C. to 145.degree. C. and a pressure to 45 psig or less
prior to contacting the first leached slurry with carbon dioxide.
[0073]The hydrothermal leaching process converts a portion of the
insoluble alkali metal compounds in the partially extracted insoluble
matter to one or more soluble alkali metal compounds, as well as
neutralizes excess alkalinity, hydrolyzes carbonates, precipitates silica
and/or alumina, and strips sulfidic sulfur as hydrogen sulfide to yield a
second leached slurry (40) comprising soluble alkali metal compounds and
a residual insoluble matter. The alkali metal in the second leached
slurry (40) comprises at least potassium carbonate and the pH of the
solution generally ranges from about 7, or about 8, or about 9, up to
about 10, or up to about 11, or up to about 12.
[0074]The hydrothermal leaching may be performed by any suitable means
known to those of skill in the art for performing hydrothermal leaching.
For example, in some embodiments, the first hydrothermal leaching step is
carried out in three pressurized continuous flow stirred tank reactors
(CSTRs) in series (in three co-current stages). In other embodiments, for
example, the first hydrothermal leaching step is carried out in a single
horizontal pressure leaching vessel with internal weirs and stirrers to
provide between 3-6 internal stages for the slurry.
[0075]The contacting of the carbon dioxide (35) with the first leached
slurry (30) may occur by any means known to those of skill in the art
suitable for introducing a gas into a slurry. Suitable methods include,
but are not limited to, solubilizing the gas under pressure with
gas-phase entrainment stirring or bubbling the gas through the slurry.
[0076]For the first hydrothermal leaching step, suitable temperatures and
pressure (including partial pressures of various gases), and the duration
of the leaching may be selected based on the knowledge of one skilled in
the art. This choice may depend on, among other factors, the composition
of the carbonaceous feedstock: Higher temperatures and/or pressures may
be more suitable for carbonaceous feedstock having higher mineral ash
content (e.g., Powder River Basin coal with 7-10% ash). Suitable
temperatures may, for example, range from about 90.degree. C., or from
about 100.degree. C., or from about 110.degree. C., up to about
120.degree. C., or up to about 130.degree. C., or up to about 140.degree.
C., or up to about 160.degree. C. The leaching is typically carried out
in the presence of steam. Suitable partial pressures of steam, for
example, range from about 3 psig, or from about 6 psig, up to about 14
psig, up to about 20 psig. Suitable total pressures, for example, range
from about 30 psig, or from about 40 psig, or from about 50 psig, up to
about 75 psig, or up to about 90 psig, or up to about 110 psig. Suitable
partial pressures of carbon dioxide may, for example, range from about 25
psig, from about 40 psig, or from about 60 psig, to about 100 psig, to
about 120 psig, to about 140 psig, or to about 170 psig. Suitable
durations, for example, range from about 15 minutes, or from about 30
minutes, or from about 45 minutes, up to about 60 minutes, or up to about
90 minutes, or up to about 120 minutes.
[0077]The hydrothermal leaching is performed in the substantial absence of
gaseous oxygen or other oxidants. For example, the leaching environment
has less than about 1% gaseous oxygen, or less than about 0.5% gaseous
oxygen, less than about 0.1% gaseous oxygen, less than about 0.01%
gaseous oxygen, or less than about 0.005% gaseous oxygen, based on the
total volume.
[0078]The first leaching process converts at least a portion, or even a
predominant portion, of the insoluble alkali metal compounds to one or
more soluble alkali metal compounds. As used in this first leaching
process, the conversion of insoluble alkali metal compounds to soluble
alkali metal compounds generally involves the chemical conversion of a
water-insoluble alkali metal compound (such as potassium aluminosilicate)
into a water-soluble alkali metal compound (such as potassium carbonate).
[0079]The amount of insoluble alkali metal compounds converted to soluble
alkali metal compounds in this leaching step will depend on a variety of
factors, including the composition of the char, the temperature, the
pressure (including the partial pressures of steam and carbon dioxide),
and the duration of the leaching operation. The amount of insoluble
alkali metal compound converted will also depend on the composition of
the insoluble alkali metal compounds present in the char. Some insoluble
alkali metal compounds, such as kaliophilite, are more difficult to
convert into soluble alkali metal compounds than others. For example, the
first leaching step may convert at least about 5%, or at least about 10%,
or at least about 20%, or at least about 40%, or at least about 50%, or
at least about 60%, or at least about 70%, or at least about 80% of the
insoluble alkali metal compounds from the insoluble matter, based on the
total moles of insoluble alkali metal compounds in the quenched char.
[0080]In some embodiments of the invention, the alkali metal hydroxide
contacting and/or the first hydrothermal leaching step is combined with
the char quenching step into a single step. In these embodiments, the
char quenching is performed at a pressure and temperature more typical
for the first hydrothermal leaching step. Suitable temperatures may, for
example, range from about 90.degree. C., or from about 100.degree. C., or
from about 110.degree. C., up to about 120.degree. C., or up to about
130.degree. C., or up to about 140.degree. C., or up to about 160.degree.
C. Suitable total pressures, for example, range from about 30 psig, or
from about 40 psig, or from about 50 psig, up to about 75 psig, or up to
about 90 psig, or up to about 110 psig. At these elevated temperatures
and pressures, the partial pressures of carbon dioxide and steam are
similar to those for the first leaching step. By performing the char
quenching under the temperature and pressure conditions typical of the
first leaching step, the two steps are effectively combined. In these
embodiments, the combined quenching/leaching step substantially leaches
the water-soluble alkali metal compounds from the insoluble matter and
converts at least a portion of the insoluble alkali metal compounds in
the char to one or more soluble alkali metal compounds, and thereby
produces a second leached slurry comprising soluble alkali metal
compounds and residual insoluble matter.
[0081]By performing the alkali metal hydroxide hydrolysis and carbonation
prior to before filtration of the slurry, the bulk of the slurry solids
will act as a filtering aid for any fine (e.g., colloidal) silica and
alumina precipitate.
4. Degassing (400)
[0082]The second leached slurry (40) is degassed under suitable pressures
and temperatures so as to remove a substantial portion of the excess
carbon dioxide and hydrogen sulfide, if present, and produce a degassed
second leached slurry (50).
[0083]Any suitable degassing methods known to those of skill in the art
may be used to perform the degassing step. The degassing may be performed
by pumping and heating the leached slurry and flashing it into a flash
drum. For these embodiments, a suitable temperature may be, for example,
about 130.degree. C. or higher, or about 140.degree. C. or higher, or
about 145.degree. C. or higher, or about 150.degree. C. or higher. For
these embodiments, after flashing into the flash drum, the slurry
temperature may drop to 120.degree. C. or less, or 110.degree. C. or
less, or 100.degree. C. or less, or 95.degree. C. or less. For these
embodiments, suitable pressures range from about 10 to about 20 psig, or
at about atmospheric pressure.
[0084]As necessary, depending on the pressure and temperature at which any
preceding steps are performed, the degassing may be performed by feeding
a heated pressurized solution into a series of staged pressure let-down
vessels equipped with stirring or other recirculation mechanisms. In some
embodiments, the slurry may be cooled prior to being fed into a first
pressure let-down vessel, for example to a suitable temperature of about
170.degree. C. or below, or to about 150.degree. C. or below, or to about
130.degree. C. or below. Suitable pressures will depend on the pressure
under which the first hydrothermal leaching was performed. Suitable
pressures for degassing are, for example, about 300 psig or less, or
about 100 psig or less, or about 50 psig or less, or about 25 psig or
less.
[0085]The off-stream gas may be handled by any means known to those of
skill in the art. For example, the off gases from a let-down vessel may
be fed, as needed, through gas/water breakdown drums and the separated
water recycled into the degassed slurry. In some embodiments, the
degassing apparatus is equipped with safety features for handling
hydrogen sulfide as an off gas.
[0086]The degassing step results in the substantial removal of excess
carbon dioxide. For example, the partial pressure of carbon dioxide is
reduced to less than about 10 psig, or less than about 5 psig, or less
than about 2 psig. The degassing also results in the substantial removal
of excess hydrogen sulfide, if present. For example, the partial pressure
of hydrogen sulfide is reduced to less than about 1 psig, or less than
about 0.1 psig, less than about 0.05 psig, or less than about 0.01 psig.
5. Separation and Recovery of Liquid from Partially Extracted Insoluble
Matter (500)
[0087]The degassed second leached slurry (50) is separated into a first
liquid stream (60) and a residual insoluble matter stream (65). The first
liquid stream comprises recovered soluble alkali metal, including soluble
alkali metal compounds that were converted from insoluble alkali metal
compounds in the char.
[0088]The residual insoluble matter steam comprises at least a portion of
the alkali metal contained in the insoluble matter of the char. For
example, the residual insoluble matter steam comprises less than about 95
molar percent, or less than about 90 molar percent, or less than about 80
molar percent, or less than about 60 molar percent, or less than about 50
molar percent, or less than about 40 molar percent, or less than about 30
molar percent, of the alkali metal contained in the insoluble matter of
the char. The residual insoluble matter stream may also comprise a
residual amount of soluble alkali metal compounds in addition to residual
insoluble alkali metal compounds.
[0089]The separation and recovery of the first liquid stream from the
residual insoluble matter stream (65) may be carried out by typical
methods of separating a liquid from a solid particulate. Illustrative
methods include, but are not limited to, filtration (gravity or vacuum),
centrifugation, use of a fluid press, decantation, and use of
hydrocyclones.
[0090]Separation and recovery steps are generally performed following
contacting of the insoluble matter with carbon dioxide and degassing to
remove excess carbon dioxide and hydrogen sulfide.
[0091]The recovered first liquid stream will contain soluble alkali metal
compounds that may be captured for reuse as a gasification catalyst.
Methods for recovery of soluble alkali metal from an aqueous solvent for
reuse as a gasification catalyst are known in the art. See, for example,
previously incorporated US2007/0277437A1.
[0092]The recovered first liquid stream comprises a predominant portion of
the soluble alkali metal compounds from the degassed second leached
slurry. For example, the first liquid stream comprises at least about 50
molar percent, or at least about 55 molar percent, or at least about 60
molar percent, or at least about 65 molar percent, or at least about 70
molar percent, of the soluble alkali metal compounds from the degassed
second leached slurry.
6. Washing (600)
[0093]Following separation from the first liquid stream, the residual
insoluble matter stream (65) is produced comprising a residual amount of
soluble alkali metal compounds in addition to residual insoluble alkali
metal compounds. The residual insoluble matter stream (65) can be washed
with an aqueous medium (70) to substantially recover the residual soluble
alkali metal compounds present in the residual insoluble matter as a
first wash stream (75). The residual soluble alkali metal compounds
consists of soluble alkali metal compounds that failed to separate into
the first liquid stream during separation (e.g., entrained aqueous
solution). The amount of entrained solution in the residual insoluble
matter stream will depend on the particle size of the residual insoluble
matter as well as the concentration of the soluble alkali metal compounds
in the entrained solution, as are familiar to those skilled in the art.
[0094]In some embodiments of the invention, the residual insoluble matter
stream is washed with an aqueous medium to produce a first wash stream
comprising at least a portion, or even a predominant portion, or
substantially all of the residual soluble alkali metal compounds in the
residual insoluble matter stream. The first wash stream may, for example,
comprise more than about 60%, or more than about 75%, or more than about
90%, or more than about 95%, of the residual alkali metal in the residual
insoluble matter stream, based on the total weight of residual alkali
metal.
[0095]As used herein, the term "washing" is not limited to a single flush
of the insoluble matter with an aqueous medium, such as water. Rather,
each washing step may include multiple staged counter-washings of the
insoluble matter. In some embodiments of the invention, the washing of
the residual insoluble matter stream comprises at least two staged
counter-washings. In some embodiments, the washing of the residual
insoluble matter stream comprises at least five staged counter-washings.
The washing may be performed according to any suitable method known to
those of skill in the art. For example, the washing step may be performed
using a continuous multi-stage counter-current system whereby solids and
liquids travel in opposite directions. As known to those of skill in the
art, the multi-stage counter current wash system may include
mixers/settlers (CCD or decantation), mixers/filters,
mixers/hydrocyclones, mixers/centrifuges, belt filters, and the like.
[0096]The first wash stream (75) is recovered by typical means of
separating a solid particulate from a liquid. Illustrative methods
include, but are not limited to, filtration (gravity or vacuum),
centrifugation, and use of a fluid press.
[0097]In some embodiments, the recovered first wash stream may be used as
at least part of the aqueous medium used for quenching the char.
EXAMPLES
Example 1
Extraction of Soluble Potassium from High-KAlSiO.sub.4 Ash Sample
[0098]An agglomerate char material was provided having a composition
especially concentrated in kaliophilite. By weight, the sample was
approximately 90% ash (including soluble and insoluble potassium) and
about 10% carbon. The material was ground to a particle size (Dp80) of
68.5 microns. The sample was subjected to water at 95.degree. C. in a
nitrogen atmosphere. The sample was filtered and dried. Analysis of the
resulting sample indicated that the amount of water-soluble potassium
removed from the sample amounted to 40.08 wt % (dry basis) of the
original sample.
Example 2
Extraction of Insoluble Potassium from High-KAlSiO.sub.4 Ash Sample
[0099]he post-treatment sample from Example 1 was used. The
hot-water-washed sample consisted of 78.20 wt % of ash and 8.99 wt %
fixed carbon. Analysis of the ash portion determined that the ash
contained 36.42 wt % of silica, 15.72 wt % of alumina, 18.48 wt % of
insoluble potassium oxide, 12.56 wt % of calcium oxide, 9.13 wt % of
ferric oxide, and trace quantities of other inorganic oxides. SEM data
confirmed that most of the insoluble potassium oxide in the ash is tied
up in KAlSiO.sub.4, primarily as kaliophilite and kalsilite.
[0100]The post-treatment sample from Example 1 was provided to a 450 ml
autoclave. KOH was added and supplemented with an amount of potassium
carbonate to simulate a recycle stream from washing, the autoclave
pressurized by the addition of CO.sub.2, and the system was heated to
200.degree. C. for 3 hours. The leached slurries were filtered, the
solids washed, and the solutions and solids analyzed to provide a
material balance on potassium. The experimental conditions yielded an
incremental extraction of the insoluble potassium species of 40%, based
on the total weight of the starting char.
Example 3
Extraction of Insoluble Potassium from Typical Char Sample
[0101]A char sample was provided from the gasification (87-89% carbon
conversion) of Class B catalyzed Powder River Basin coal. The dry sample
was determined to contain 34.4 wt % potassium. The char sample was
crushed and added to water to form a slurry in a nitrogen atmosphere. The
slurry sample was added to an autoclave with KOH and additional water.
The system was pressurized with CO.sub.2 and heated for 90 minutes at
160.degree. C. The autoclave was cooled to ambient temperature. The solid
was filtered and washed three times with water. Thus, the soluble
potassium was largely removed from the sample. The total potassium
extraction was 92.0%.
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