AU2021295775A1 - Method for fixing carbon dioxide - Google Patents
Method for fixing carbon dioxide Download PDFInfo
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- AU2021295775A1 AU2021295775A1 AU2021295775A AU2021295775A AU2021295775A1 AU 2021295775 A1 AU2021295775 A1 AU 2021295775A1 AU 2021295775 A AU2021295775 A AU 2021295775A AU 2021295775 A AU2021295775 A AU 2021295775A AU 2021295775 A1 AU2021295775 A1 AU 2021295775A1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/62—Carbon oxides
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/50—Carbon dioxide
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D9/00—Crystallisation
- B01D9/02—Crystallisation from solutions
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- Oil, Petroleum & Natural Gas (AREA)
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Abstract
This method for fixing carbon dioxide comprises: a first step S1 for passing seawater or saline water through a nanofiltration membrane to produce an NF membrane concentrated liquid that is concentrated without permeating the nanofiltration membrane; a second step S2 for precipitating and collecting, from the NF membrane concentrated liquid produced in the first step S1, at least one crystal, which is selected from among calcium sulfate, sodium chloride, potassium chloride, and sodium sulfate; a third step S3 for obtaining an alkaline earth metal oxide from the NF membrane concentrated liquid that has undergone the second step S2; and a fourth step S4 for reacting carbon dioxide with the alkaline earth metal oxide obtained in the third step S3, and thereby fixing the carbon dioxide as carbonate.
Description
Technical Field
[0001]
The present invention relates to a method for fixing carbon dioxide to an
alkaline earth metal.
Background Art
[0002]
As global warming becomes more serious, an increase in temperature is
required to be suppressed, and as an evaluation model thereof, the goal is to reduce an
anthropogenic carbon dioxide (C02) emission amount to zero. Examples of means for
achieving the above goal include a C02 fixing method.
Examples of effective means of the C02 fixing method include a method in
which C02 is fixed by bonding Mg or Ca which is an alkaline earth metal to the C02.
However, the conventional method using an ore containing the alkaline earth metal
requires a treatment associated with C02 emission such as high temperature and high
pressure or addition of chemicals, and thus, in many cases, the C02 is emitted in the
entire process.
Mg and Ca are also contained in seawater and waste brackish water from a
desalination plant of the seawater. For example, a C02 fixing method using seawater
has been proposed (see, for example, Patent Literatures 1 and 2).
Citation List
Patent Literature
[0003]
Patent Literature 1: JP 2005-21870 A
Patent Literature 2: JP 2010-125354 A
Summary of Invention
Technical Problem
[0004]
In the C02 fixing method using seawater or brackish water, many methods in
which C02 is injected into seawater or brackish water have been studied. However,
the methods have a problem that the efficiency of C02 fixation in a liquid phase
decreases due to the presence of a strong hydration shell formed around Mg2+ ions
which are divalent cations having a small ion diameter, and cations (Na*, K) which
compete with the Mg2+ ions in carbonation. As a solution therefor, means for
increasing a pH by the addition of an alkali such as Ca(OH)2, which is difficult to
recycle, have been mainly used. However, these means for promoting the reaction
with C02 have increased C02 emission in the entire process in consideration of energy
consumption and C02 emission due to additive production as life cycle assessment.
Also in the techniques of Patent Literatures 1 and 2, pH adjustment and a
wastewater treatment and the like are required, which make it difficult to reduce the
C02 emission amount as the entire process.
As described above, the problem point of the C02 fixing method using
seawater or brackish water includes the inhibition of the reaction with the C02 due to
the presence of molecules or ions other than Mg and Ca. Therefore, in a process of
separating Mg and Ca from seawater or brackish water, C02 reduction capability must
be evaluated in consideration of C02 emission derived per unit operation.
[0005]
Therefore, the present invention provides a method for fixing carbon dioxide
to an alkaline earth metal, which enhances carbon dioxide reduction capability while
considering the carbon dioxide emission amount.
Solution to Problem
[0006]
The object of the present invention is achieved by a method for fixing carbon
dioxide including: a first step of causing seawater or brackish water to pass through a
nanofiltration membrane to produce an NF membrane-concentrated liquid concentrated
without permeating the nanofiltration membrane; a second step of precipitating and
collecting at least one crystal selected from calcium sulfate, sodium chloride, potassium
chloride, and sodium sulfate from the NF membrane-concentrated liquid produced in
the first step; a third step of obtaining an alkaline earth metal oxide from the NF
membrane-concentrated liquid subjected to the second step; and a fourth step of reacting
the alkaline earth metal oxide obtained in the third step with carbon dioxide to fix the
carbon dioxide as a carbonate.
[0007]
In the method for fixing carbon dioxide, the second step preferably includes a
first concentration crystallization step of adding calcium sulfate as a seed crystal to the
NF membrane-concentrated liquid, followed by evaporating and concentrating to
precipitate and collect the calcium sulfate crystal. In the first concentration
crystallization step, the collected calcium sulfate crystal is preferably used as the seed
crystal. The second step preferably includes a second concentration crystallization
step of further evaporating and concentrating the NF membrane-concentrated liquid
after collecting the calcium sulfate crystal to precipitate and collect the sodium chloride
crystal.
[0008]
The second step preferably includes a cooling crystallization step of collecting
a crystal precipitated by cooling and crystallizing the NF membrane-concentrated liquid.
The cooling crystallization step preferably includes: a first cooling crystallization step
of collecting the potassium chloride crystal precipitated by cooling and crystallizing the
NF membrane-concentrated liquid; and a second cooling crystallization step of
collecting the sodium sulfate crystal precipitated by cooling and crystallizing the NF
membrane-concentrated liquid subjected to the first cooling crystallization step at a
temperature lower than a cooling crystallization temperature of the first cooling
crystallization step.
[0009]
The first step preferably includes a pH adjusting step of adjusting a pH of the
produced NF membrane-concentrated liquid by adding an acid to the NF membrane
concentrated liquid.
[0010]
The first step preferably includes a salt making step of collecting a sodium
chloride crystal precipitated by concentrating an NF membrane-permeated liquid
permeating the nanofiltration membrane. The first step preferably includes a merging
step of merging a blow liquid after the sodium chloride crystal is collected in the salt
making step with the produced NF membrane-concentrated liquid. The first step
preferably includes a pH adjusting step of adjusting a pH of the produced NF
membrane-concentrated liquid by adding an acid solution to the NF membrane
concentrated liquid, the acid solution obtained by electrodialyzing a solution of the
sodium chloride crystal produced in the salt making step.
[0011]
The alkaline earth metal oxide obtained in the third step preferably contains
magnesium oxide.
Advantageous Effects of Invention
[0012]
The present invention can provide a method for fixing carbon dioxide to an
alkaline earth metal, which enhances carbon dioxide reduction capability while
considering the carbon dioxide emission amount.
Brief Description of Drawings
[0013]
FIG. 1 is a process flow diagram for illustrating a method for fixing carbon
dioxide according to an embodiment of the present invention.
FIG. 2 is a diagram showing examples of changes in amounts of various ions
in a process flow shown in FIG. 1.
FIG. 3 is a diagram showing a modification of some steps in the process flow
shown in FIG. 1.
Description of Embodiments
[0014]
A method for fixing carbon dioxide of the present invention provides a
method for fixing carbon dioxide to an alkaline earth metal contained in seawater or
brackish water. In the present embodiment, the "alkaline earth metal" means a broad
range including Mg and Be which are elements of the second group of the periodic table
in addition to Ca, Sr, Ba, and Ra. In particular, at least Mg is preferably contained as
the alkaline earth metal from the viewpoint of the easiness of a reaction with C02 and
the viewpoint that a carbonate obtained by the reaction can be expected to be used for
various applications.
[0015]
The "seawater or brackish water" is an aqueous solution containing ions of
alkaline earth metals such as magnesium ions (Mg2+) and calcium ions (Ca2+). The
seawater or brackish water contains ions constituting at least one crystal selected from
calcium sulfate, sodium chloride, potassium chloride, and sodium sulfate, in addition to
the ions of alkaline earth metals. Specifically, the seawater or brackish water contains
at least one kinds of ions selected from chloride ions (Cl-), sulfate ions (SO42-), sodium
ions (Na*), and potassium (K).
[0016]
As the seawater or brackish water, those obtained from at least one selected
from seawater, a salt lake, and industrial wastewater can be used. If the alkaline earth
metal is contained, in addition to the seawater, the salt lake, and the industrial
wastewater, river water, rainwater, sewage water treatment water, and associated water
of oil fields and gas fields, and the like can also be used. More specific examples of
the brackish water include water produced from a salt lake or the like, waste brackish
water discharged by a desalination or salt production process, collection of a valuable
substance from seawater and a salt lake or the like, and industrial wastewater from a
chemical factory or the like.
[0017]
The brackish water is preferably at least one selected from brackish water
obtained from a water production device using seawater, brackish water obtained from a
process for making a salt from seawater, and brackish water obtained from a process for
collecting lithium from a salt lake from the viewpoint of containing a large amount of
Mg, easily reducing an environmental load, and easily reducing a C02 emission amount.
[0018]
Hereinafter, an embodiment of the present invention will be described with
reference to the accompanying drawings. FIG. 1 is a process flow diagram for
illustrating a method for fixing carbon dioxide according to an embodiment of the
present invention. In the present embodiment, the treatment target is seawater, but a
similar treatment can be performed in the case of brackish water. As shown in FIG. 1,
a method for fixing carbon dioxide of the present embodiment includes: a first step SI
of causing seawater to pass through a nanofiltration membrane (NF membrane) to
produce an NF membrane-concentrated liquid concentrated without permeating the NF
membrane; a second step S2 of precipitating and collecting at least one crystal selected
from calcium sulfate, sodium chloride, potassium chloride, and sodium sulfate from the
NF membrane-concentrated liquid produced in the first step Sl; a third step S3 of
obtaining an alkaline earth metal oxide from the NF membrane-concentrated liquid
subjected to the second step S2; and a fourth step S4 of reacting the alkaline earth metal
oxide obtained in the third step S3 with carbon dioxide to fix the carbon dioxide as a
carbonate.
[0019]
<SI: First Step>
In the first step S1, the seawater is supplied to an NF membrane unit by an
intermediate-pressure pump or the like to pass through the NF membrane, thereby
producing an NF membrane-permeated liquid permeating the NF membrane and an NF
membrane-concentrated liquid concentrated without permeating the NF membrane.
[0020]
Since the NF membrane has a property of suppressing the permeation of
divalent or higher ions and causing monovalent ions to easily permeate, most of an
alkaline earth metal for fixing the carbon dioxide remains in the NF membrane concentrated liquid, and the concentrations of Na' and K+ and the like which may hinder the fixation are reduced. This makes it possible to easily and efficiently fix the carbon dioxide to the alkaline earth metal contained in the seawater (or brackish water), whereby the generation of the carbon dioxide in the entire process including post-steps can be suppressed. FIG. 2 shows examples of amounts of various ions (mg/h) contained in the seawater, the NF membrane-permeated liquid, and the NF membrane concentrated liquid when the seawater is supplied at a flow rate of 100 m3 /h.
[0021]
<S11: Salt Making Step>
Meanwhile, since the NF membrane-permeated liquid contains a large amount
of monovalent ions Na' and Cl-, the first step S of the present embodiment includes a
salt making step SlIof collecting a sodium chloride (NaCl) crystal precipitated by
concentrating the NF membrane-permeated liquid. The salt making step S1 Iof the
present embodiment includes a membrane treatment step S Illof supplying the NF
membrane-permeated liquid to a reverse osmosis membrane (RO membrane) unit by a
high pressure pump or the like and causing the NF membrane-permeated liquid to pass
through the RO membrane to produce a membrane treatment-concentrated liquid
concentrated without permeating the RO membrane, and a crystallization step S112 of
supplying the produced membrane treatment-concentrated liquid to a crystallizer and
heating and evaporating the liquid to precipitate a NaCl crystal. Steam discharged
from the crystallizer is condensed in a condenser or the like to become distilled water.
The distilled water is merged with the membrane treatment permeated liquid permeating
the RO membrane, and is used as produced water or the like. Apart of a crystallizer
concentrated liquid concentrated in the crystallizer is discharged from the crystallizer as
a slurry liquid containing the NaCl crystal, and dehydrated by a centrifugal separator or the like to collect the NaCl crystal. Since the NF membrane-permeated liquid hardly contains SO42-, the NF membrane-permeated liquid can be concentrated at a high concentration by the low-energy membrane treatment step S11.
[0022]
The membrane treatment step S Illis not limited to the treatment using the
RO membrane. The membrane treatment step Sillmay be another treatment using a
semipermeable membrane, or a combination of a plurality of membrane treatments.
For example, as shown in FIG. 3, the membrane treatment step Sillcan include an RO
membrane concentration step S113 of concentrating the NF membrane-permeated liquid
with the RO membrane to produce an RO membrane-concentrated liquid, and a
composite membrane treatment step S114 of supplying the RO membrane-concentrated
liquid to a high-pressure chamber of a semipermeable membrane unit separated by a
semipermeable membrane, and further concentrating the RO membrane-concentrated
liquid using a pressure difference from a collected liquid passing through a low-pressure
chamber. As the collected liquid supplied to the low-pressure chamber, a part of the
RO membrane-concentrated liquid passing through the high-pressure chamber can be
used, and the collected liquid passing through the low-pressure chamber can be merged
with the NF membrane-permeated liquid before the RO membrane concentration step
S113. As shown in FIG. 3, an evaporation treatment step S115 of evaporating and
concentrating the membrane treatment-concentrated liquid produced in the membrane
treatment step Si llby a horizontal tube evaporator or the like may be provided
between the membrane treatment step Si land the crystallization step S112.
[0023]
<S12: Merging Step>
A liquid after the NaCl crystal is collected in the salt making step Sli is discharged as a blow liquid. The first step Si of the present embodiment includes a merging step S12 of merging the blow liquid with the NF membrane-concentrated liquid, whereby the discharge of a waste liquid to the outside of the system can be suppressed to reduce the environmental load. Since the alkaline earth metal to be collected such as magnesium is contained not only in the NF membrane-concentrated liquid but also in the blow solution which is the NF membrane-permeated liquid, the collection rate of the alkaline earth metal required for fixing the carbon dioxide in post steps can be increased by providing the above-described merging step S12.
[0024]
<S13: pH Adjusting Step>
The first step S Iof the present embodiment includes a pH adjusting step S13
for adjusting the pH of the NF membrane-concentrated liquid with which the blow
liquid is merged in the merging step S12. ThepH adjusting step S13 is a step of
adding a pH adjusting agent such as hydrochloric acid (HCl) to the NF membrane
concentrated liquid to set the pH value of the NF membrane-concentrated liquid to an
acidic side. This makes it possible to suppress the production of a soft scale such as
magnesium hydroxide (Mg(OH)2) or calcium carbonate (CaCO3) in the second step S2
to be described later. The pH value of the NF membrane-concentrated liquid after the
pH adjustment is preferably 3.5 to 6.5.
[0025]
The pH adjusting step S13 includes an electrodialysis step S131 of
electrodialyzing the NaCl crystal produced in the salt making step Sll, whereby HCl
produced in the electrodialysis step S131 can be used as a pH adjusting agent. The
electrodialysis step S131 can use, for example, a bipolar membrane electrodialyzer, and
separates a NaCl solution into a HCl solution and a NaOH solution. As described above, the pH adjusting agent is produced by electrodialysis using the crystal obtained in the salt making step Si1. This has no possibility that C02 is separately generated in the production process of the pH adjusting agent, and makes it possible to perform electrodialysis using renewable energy or the like, whereby C02 emission in the entire process can be suppressed.
[0026]
<S2: Second Step>
The second step S2 is a step of removing impurities which hinder the fixation
of the carbon dioxide to the alkaline earth metal to be described later from the NF
membrane-concentrated liquid produced in the first step S Ito facilitate the isolation of
the alkaline earth metal oxide in the third step S3. The second step S2 includes a first
concentration crystallization step S21 of adding calcium sulfate as a seed crystal to the
NF membrane-concentrated liquid, followed by evaporating and concentrating to
precipitate and collect the calcium sulfate crystal, a second concentration crystallization
step S22 of further evaporating and concentrating the NF membrane-concentrated liquid
after collecting the calcium sulfate crystal to precipitate and collect the sodium chloride
crystal, and a cooling crystallization step S23 of collecting a crystal precipitated by
cooling and crystallizing the NF membrane-concentrated liquid.
[0027]
<S21: First Concentration Crystallization Step>
In the first concentration crystallization step S21, the NF membrane
concentrated liquid is supplied to a first concentration can, and heated to be evaporated
and concentrated, whereby the calcium sulfate crystal (CaSO 4 2H20) is precipitated.
Then, the NF membrane-concentrated liquid is discharged as a slurry liquid, and the
calcium sulfate crystal is separated by a solid-liquid separator such as a centrifugal separator. The NF membrane-concentrated liquid contains Ca2, Na+, and K+ and the like, but the calcium sulfate crystal has inverse solubility in which solubility decreases with an increase in temperature, and thus an operation temperature for evaporating and concentrating is maintained so that Ca2+ is precipitated while Na+ and K' are not precipitated. The operation temperature is preferably 70 to 90°C, and is set to, for example, 80°C.
[0028]
In the first concentration crystallization step S21, in order to prevent the scale
generation of the calcium sulfate, it is preferable to add a seed crystal of CaSO 4 -2H20 to
the first evaporation can to promote crystal growth with the seed crystal as a core. For
this seed crystal, CaSO 4 -2H20 produced in thefirst concentration crystallization step
S21 can be preferably used. The NF membrane-concentrated liquid is on an acidic
side in the pH adjusting step S13, whereby the scale generation of the calcium sulfate
can be suppressed.
[0029]
<S22: Second Concentration Crystallization Step>
The second concentration crystallization step S22 is performed by supplying
the NF membrane-concentrated liquid subjected to thefirst concentration crystallization
step S21 to a second concentration can, heating the NF membrane-concentrated liquid
to further evaporate and concentrate the NF membrane-concentrated liquid, thereby
precipitating a crystal containing sodium chloride (NaCl) as a main component, and
then causing a solid-liquid separator to separate the sodium chloride crystal. An
operating temperature for evaporating and concentrating is preferably 60 to 80°C, and is
set to, for example, 70°C. A concentration ratio in the second concentration
crystallization step S22 is preferably set to a range in which MgCl2 is not precipitated such that the collection rate of the alkaline earth metal oxide mainly containing magnesium oxide can be increased in the third step S3 to be described later.
[0030]
<S23: Cooling Crystallization Step>
The cooling crystallization step S23 is performed by supplying the NF
membrane-concentrated liquid subjected to the second concentration crystallization step
S22 to a cooling crystallization can, cooling the NF membrane-concentrated liquid to a
predetermined cooling crystallization temperature while stirring the NF membrane
concentrated liquid to precipitate a crystal of an intended impurity, and then causing a
solid-liquid separator to separate the crystal. The cooling crystallization step S23 of
the present embodiment preferably includes: a first cooling crystallization step S231 of
collecting a potassium chloride crystal precipitated by cooling and crystallizing the NF
membrane-concentrated liquid; and a second cooling crystallization step S232 of
collecting a sodium sulfate crystal precipitated by cooling and crystallizing the NF
membrane-concentrated liquid subjected to the first cooling crystallization step S231 at
a temperature lower than a cooling crystallization temperature of the first cooling
crystallization step S231. The cooling crystallization temperature of the first cooling
crystallization step S231 is a temperature at which a crystal mainly containing KCl is
precipitated but a crystal of Na2SO4-10 H 2 0 is not precipitated. Thecooling
crystallization temperature is preferably 33 to 40°C, and is set to, for example, 36°C.
The cooling crystallization temperature of the second cooling crystallization step S232
is a temperature at which the crystal of Na2SO4-10H 2 0 is precipitated, and is set to, for
example, 0 to 10°C.
[0031]
Thus, the NF membrane-concentrated liquid subjected to the first concentration crystallization step S21, the second concentration crystallization step S22, and the cooling crystallization step S23 is brine containing an alkaline earth metal chloride such as MgCl2 as a main component. In the second step S2, it is not necessary to perform all of the first concentration crystallization step S21, the second concentration crystallization step S22, and the cooling crystallization step S23, and only necessary steps may be appropriately selected according to components of seawater or brackish water to be treated so that at least one crystal selected from calcium sulfate, sodium chloride, potassium chloride, and sodium sulfate can be precipitated and collected from the NF membrane-concentrated liquid.
[0032]
<S3: Third Step>
The third step S3 is a step of obtaining an alkaline earth metal oxide from the
brine containing the alkaline earth metal chloride such as MgCl2 obtained in the second
step S2 as a main component, and includes a drying step S31 and a thermal
decomposition step S32.
[0033]
<S31: Drying Step>
The brine obtained in the second step S2 of the present embodiment is a slurry
containing magnesium chloride (MgC2) hydrate as a main component, and is dried in
the drying step S31 to form magnesium chloride dihydrate (MgC2-2H20). A drying
temperature in the drying step S31 is preferably 130°C or lower, and more preferably
100 to 129°C under the atmospheric pressure for the production of MgCl2-2H20.
[0034]
<S32: Thermal Decomposition Step>
In the thermal decomposition step S32, at least a part of MgCl2-2H20 produced in the drying step S31 is thermally decomposed to produce hydroxy magnesium chloride (MgOHCl), and the MgOHCl is further thermally decomposed for dehydrochlorination to produce magnesium oxide (MgO). A thermal decomposition temperature in the thermal decomposition step S32 is preferably 235°C or lower, and more preferably 160 to 235°C under the atmospheric pressure for the production of the
MgOHCl. If the pressure is made lower than the atmospheric pressure, the
temperature can be further lowered. For the production of the MgO, the temperature is
preferably 300 to 500°C, and more preferably 350 to 450°C under the atmospheric
pressure. If the pressure is made lower than the atmospheric pressure, the temperature
can be further lowered.
[0035]
In the thermal decomposition step S32, an HCl gas is discharged when the
MgO is produced, whereby the HCl gas may be collected and reused. This HCl gas
can be used, for example, as the pH adjusting agent in the pH adjusting step S13,
whereby C02 emission due to the separate production of HCl can be avoided.
[0036]
<S4: Fourth Step>
The fourth step S4 is a step of reacting the alkaline earth metal oxide such as
MgO obtained in the third step S3 with carbon dioxide to fix the carbon dioxide as a
carbonate. The carbon dioxide is fixed to the alkaline earth metal oxide by a solid-gas
reaction between the alkaline earth metal oxide and the carbon dioxide-containing gas.
The carbon dioxide-containing gas may be atmospheric air, or an exhaust gas of various
combustion apparatuses, or the like. The concentration of the carbon dioxide
contained in the gas is not limited, but the concentration of the carbon dioxide contained
in the gas is about atmospheric air to 100% by volume from the viewpoint of the easiness of the progression of the solid-gas reaction. When MgO is reacted with C02, magnesium carbonate trihydrate (MgCO3 3H 2 0) is formed, and the carbon dioxide is fixed. The method for fixing carbon dioxide as a carbonate in the fourth step S4 is not limited to the above method, and for example, it is also possible to dissolve the alkaline earth metal oxide such as MgO obtained in the third step S3 in water to produce an aqueous solution, and bring the aqueous solution into gas-liquid contact with carbon dioxide by bubbling or the like to fix the carbon dioxide to the alkaline earth metal oxide.
[0037]
According to the present invention, the seawater or brackish water is the
aqueous solution containing a plurality of ions as described above, whereby water (pure
water), salt, gypsum, and potassium chloride and the like can be obtained as by
products in each step described above. Therefore, in addition to C02 fixation, various
by-products are produced, and these can be expected to be used for more
environmentally friendly products. The present invention can use the waste liquid as
the brackish water as described above, whereby the present invention can be used as a
waste liquid treatment, and is considered to contribute to the reduction of waste liquid
treatment cost. Furthermore, the magnesium carbonate to which the carbon dioxide is
fixed can also be used as a building material. Therefore, the present invention can also
provide a method for producing an alkaline earth metal carbonate using the above
described method for fixing carbon dioxide.
Reference Signs List
[0038]
Sl first step
Sil salt making step
S12 merging step
S13 pH adjusting step
S2 second step
S21 first concentration crystallization step
S22 second concentration crystallization step
S23 cooling crystallization step
S3 third step
S4 fourth step
Claims (11)
1. A method for fixing carbon dioxide comprising:
a first step of causing seawater or brackish water to pass through a
nanofiltration membrane to produce an NF membrane-concentrated liquid concentrated
without permeating the nanofiltration membrane;
a second step of precipitating and collecting at least one crystal selected from
calcium sulfate, sodium chloride, potassium chloride, and sodium sulfate from the NF
membrane-concentrated liquid produced in the first step;
a third step of obtaining an alkaline earth metal oxide from the NF membrane
concentrated liquid subjected to the second step; and
a fourth step of reacting the alkaline earth metal oxide obtained in the third
step with carbon dioxide to fix the carbon dioxide as a carbonate.
2. The method according to claim 1, wherein the second step includes a first
concentration crystallization step of adding calcium sulfate as a seed crystal to the NF
membrane-concentrated liquid, followed by evaporating and concentrating to precipitate
and collect the calcium sulfate crystal.
3. The method according to claim 2, wherein in the first concentration
crystallization step, the collected calcium sulfate crystal is used as the seed crystal.
4. The method according to claim 2 or 3, wherein the second step includes a
second concentration crystallization step of further evaporating and concentrating the
NF membrane-concentrated liquid after collecting the calcium sulfate crystal to
precipitate and collect the sodium chloride crystal.
5. The method according to any one of claims 1 to 4, wherein the second step
includes a cooling crystallization step of collecting a crystal precipitated by cooling and
crystallizing the NF membrane-concentrated liquid.
6. The method according to claim 5, wherein the cooling crystallization step
includes: a first cooling crystallization step of collecting the potassium chloride crystal
precipitated by cooling and crystallizing the NF membrane-concentrated liquid; and a
second cooling crystallization step of collecting the sodium sulfate crystal precipitated
by cooling and crystallizing the NF membrane-concentrated liquid subjected to the first
cooling crystallization step at a temperature lower than a cooling crystallization
temperature of the first cooling crystallization step.
7. The method according to any one of claims 1 to 6, wherein the first step
includes a pH adjusting step of adjusting a pH of the produced NF membrane
concentrated liquid by adding an acid to the NF membrane-concentrated liquid.
8. The method according to any one of claims I to 7, wherein the first step
includes a salt making step of collecting the sodium chloride crystal precipitated by
concentrating an NF membrane-permeated liquid permeating the nanofiltration
membrane.
9. The method according to claim 8, wherein the first step includes a merging
step of merging a blow liquid after the sodium chloride crystal is collected in the salt
making step with the produced NF membrane-concentrated liquid.
10. The method according to claim 8 or 9, wherein the first step includes a pH
adjusting step of adjusting a pH of the produced NF membrane-concentrated liquid by
adding an acid solution to the NF membrane-concentrated liquid, the acid solution
obtained by electrodialyzing a solution of the sodium chloride crystal produced in the
salt making step.
11. The method according to any one of claims 1 to 10, wherein the alkaline earth
metal oxide obtained in the third step contains magnesium oxide.
Fig. 1 NF MEMBRANE- PERMEATED LIQUID MEMBRANE TREATMENT SEAWATER PERMEATED LIQUID PRODUCED (OR BRACKISH 海水 WATER WATER) (又はかん水) MEMBRANE DISTILLED NF TREATMENT WATER MEMBRANE- CONCENTRATED CONCENTRATED LIQUID ELECTRO- CRYSTALLIZE LIQUID DIALYZE
BLOW LIQUID
1/2 ADJUST DRAWINGS
pH S23 MgCl2 S31 S32 S3 S21 S22 S231 S232 (MAIN COMPO- FIRST SECOND FIRST SECOND NENT) CONCENT- CONCENT- COOLING COOLING BRINE THERMALLY DRY RATION RATION CRYSTALLI- CRYSTALLI- DECOMPOSE CRYSTALLI CRYSTALLI- ZATION ZATION -ZATION ZATION MgO CaSO4・2H2O KCI (MAIN COMPONENT) NaCl AND THE LIKE FIX CO2
NaCl (MAIN COMPONENT) Na2SO4・10H2O KCI AND THE LIKE CO2 S4
S2
Fig. 2
NF NF MEMBRANE- MEMBRANE- SEAWATER PERMEATED CONCENTRATED LIQUID LIQUID
Mg 2+ 140 42 98
Ca 2+ 40 21 19
Na + 1070 731 339
K+ 40 27 13 - Cl 1900 1281 619
SO 42- 235 1 234
Fig. 3
NF S113 MEMBRANE- PRODUCED PERMEATED WATER LIQUID RO MEMBRANE- CONCENTRATED S115 LIQUID S114 EVAPORATION TREATMENT
TO CRYSTALLIZATION STEP S112 S111
2/2
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