KR101793809B1 - Crystallization reactor - Google Patents
Crystallization reactor Download PDFInfo
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- KR101793809B1 KR101793809B1 KR1020157033811A KR20157033811A KR101793809B1 KR 101793809 B1 KR101793809 B1 KR 101793809B1 KR 1020157033811 A KR1020157033811 A KR 1020157033811A KR 20157033811 A KR20157033811 A KR 20157033811A KR 101793809 B1 KR101793809 B1 KR 101793809B1
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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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D9/00—Crystallisation
- B01D9/0036—Crystallisation on to a bed of product crystals; Seeding
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D9/00—Crystallisation
- B01D9/005—Selection of auxiliary, e.g. for control of crystallisation nuclei, of crystal growth, of adherence to walls; Arrangements for introduction thereof
- B01D9/0054—Use of anti-solvent
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F2001/5218—Crystallization
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/105—Phosphorus compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/12—Halogens or halogen-containing compounds
- C02F2101/14—Fluorine or fluorine-containing compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/44—Time
Abstract
And a crystallization reaction unit (10) having a crystallization reaction unit (28) for generating crystals of a poorly soluble salt by adding a calcium agent to the raw water containing the crystallization target substance. In the crystallization reaction tank (10) There is provided a solid liquid separating section 30 in which an inner peripheral wall 26 opposed to the outer peripheral wall is disposed and an upward flow is formed between the inner peripheral wall and the outer peripheral wall to carry out solid- The valve 18 provided in the raw water supply line 16 is opened so that the passage time of the raw water to the raw water supply line 16 is not less than 1/2 times and not more than 5 times the residence time of the raw liquid in the solid- The water supply stopping time of the raw water to the crystallization reaction tank 10 after the water feed is set to 1/5 times to 1 time or less of the residence time in the solid- 18) is used.
Description
The present invention relates to a crystallization reaction apparatus for treating crystallization (i.e., crystallization) substances such as fluorine, phosphorus and the like as insoluble salts.
Conventionally, as a method for recovering and reusing a poorly soluble salt such as calcium fluoride or calcium phosphate, a crystallization method or the like can be used. As the crystallization method, for example, when fluorine in the fluorine-containing raw water is recovered as calcium fluoride, the fluorine-containing raw water is introduced into the reaction tank and calcium carbonate is injected into the reaction tank to react them. And a method of precipitating calcium fluoride.
Conventionally, the crystallization method includes a flow-bottomed crystallization reaction apparatus (for example, a method in which a raw material containing a crystallization target substance such as fluorine-containing raw water is supplied as an upward flow into a reaction tank and subjected to treatment while flowing crystals of a poorly soluble salt in the reaction tank (Reference 1)), a stirring-type crystallization reaction apparatus (for example, Patent Document 2) in which a stirrer is provided in a reaction tank and the solution of the poorly soluble salt in the reaction tank is flowed by stirring the stirring tank. Generally, when the crystal of the poorly soluble salt in the reaction tank grows to some extent, the withdrawing step of extracting a part of the crystals of the insoluble salt and the replenishment step of replenishing the seed crystal are repeatedly performed in the reaction tank, A method of obtaining crystals of a salt has been adopted.
In order to recover the poorly soluble salt at a high recovery rate in the crystallization reaction apparatus, it is necessary to keep the surface area of the poorly soluble salt crystals and the like high in the reaction tank, that is, to maintain the particles of the poorly soluble salt crystals in the reaction tank at a fine particle diameter It is important to do. As a method for finely holding the particles (particle diameter distribution) of the poorly soluble salt crystals in the reaction tank, it is considered to supply a large number of seed crystals having a fine particle diameter distribution in the reaction tank. However, .
It is therefore an object of the present invention to provide a crystallite reaction apparatus capable of recovering a poorly soluble salt at a high recovery rate without increasing the amount of seed crystals to be supplied.
(1) The crystallite reaction apparatus of the present invention comprises stirring means having a stirring blade, a crystallization reaction vessel having a crystallization reaction section for adding a calcium agent to raw water containing a crystallization substance to produce crystals of the insoluble salt, Wherein an inner peripheral wall facing the outer peripheral wall of the crystallization reaction vessel is disposed in the crystallization reaction vessel so as to form an upward flow between the inner peripheral wall and the outer peripheral wall, And a solid-liquid separating section for performing solid-liquid separation of the treated water, wherein the water passing means intermittently circulates the raw water to the crystallization reacting section.
(2) In the crystallization reaction apparatus described in (1) above, the water supply time of the raw water at the time of intermittent water passing by the water passing means is not less than 1/2 times and not more than 5 times the residence time in the solid- , And the water stopping time of the raw water at the time of intermittent passing by the water passing means is preferably one fifth or more and one time or less of the residence time in the solid-liquid separating portion.
(3) In the crystallization reaction device described in (1) above, the water supply time of the raw water at the time of intermittent passing by the water passing means is at least 1 time and at most 4 times the residence time at the solid- It is more preferable that the water stopping time of the raw water at the time of intermittent passing by the water sending means is 1/4 times or more and 1/2 times or less of the residence time in the solid-liquid separating portion.
(4) In the crystallization reaction apparatus according to any one of (1) to (3), an outlet for discharging the treated water is formed on an outer peripheral wall of the crystallization reaction vessel provided with the solid- Wherein the upper end of the peripheral wall is at the same height as the discharge port or at a position lower than the discharge port in such a manner that a part of the treatment water can be discharged from the discharge port and a part of the treated water in the solid- And is conveyed to the crystallization reaction section.
According to the present invention, the insoluble salt can be recovered at a high recovery rate without increasing the amount of seed crystals to be supplied.
1 is a schematic diagram showing an example of a crystallization reaction apparatus according to an embodiment of the present invention;
Fig. 2 is a schematic diagram showing an example of the constitution of the crystallization reaction apparatus of Reference Example; Fig.
3 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Example 1;
4 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Example 2;
5 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Example 3;
6 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Example 4;
7 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Comparative Example 1;
8 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Comparative Example 2;
9 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Comparative Example 3. Fig.
Embodiments of the present invention will be described below. The present embodiment is an example of carrying out the present invention, and the present invention is not limited to this embodiment.
1 is a schematic diagram showing an example of a crystallization reaction apparatus according to an embodiment of the present invention. 1, the crystallization reaction apparatus 1 comprises a
A raw
In the
The
The
The operation of the crystallization reaction apparatus 1 according to the present embodiment will be described.
First, the
In the
Crystals of the poorly soluble calcium salt such as calcium fluoride or calcium phosphate produced in the
On the other hand, the treated water after the crystallization reaction in the
Here, if the flow of the raw water to the
Thus, in the present embodiment, the recovery rate of crystals of the poorly soluble calcium salt is improved by intermittently circulating the raw water to the
Normally, it is considered that it is difficult to stably operate the apparatus while securing the recovery rate of the poorly soluble salt crystals. However, the apparatus configuration of the present embodiment is adopted, and while the apparatus is operated, The crystals of the refractory calcium salt having a fine particle diameter are retained in the
First, the
If the water supply time of the raw water to the
Next, a crystal of a poorly soluble calcium salt which is not separated from the treated water in the solid-
For example, fine particles such as crystals of an insoluble calcium salt that can not be precipitated on the surface of the seed crystal can not be completely separated by the solid-
1, the upper end of the inner
When the upper end of the inner
Next, other conditions and the like of the crystallization reaction apparatus 1 of the present embodiment will be described.
In the present embodiment, it is preferable that the addition (injection point) of the calcium agent and raw water to the
In the present embodiment, it is preferable to provide the
Further, as described above, when the
The crystals having a larger particle diameter due to the crystallization reaction do not rise according to the upward flow of the outer circumferential portion of the tube but sink downward and do not enter the
In the present embodiment, it is preferable to add an acid or an alkali to the
The raw water containing the crystallization target substance such as fluorine, phosphorus, etc. in the present embodiment may be any raw water as long as it contains fluorine, phosphorus or the like which is removed by crystallization treatment. For example, Raw water discharged from industry, power plant, aluminum industry, and the like.
The fluorine, phosphorus, or the like which is the crystallization target substance can be present in the raw water in any state as long as it is crystallized by the crystallization reaction. From the viewpoint of being dissolved in the raw water, it is preferable that the crystallization target substance is ionized.
As the calcium agent used in the present embodiment, for example, calcium chloride, calcium hydroxide and the like are used. The form of adding the calcium agent may be a powder state or a slurry state.
The amount of the calcium agent to be injected is preferably 0.8 to 2 times, and 1 to 2 times, more preferably 1 to 1.2 times as large as the chemical equivalent of calcium. If the chemical equivalent of calcium is more than twice the chemical equivalent of fluorine and phosphorus of the raw water, calcium fluoride and calcium phosphate are not precipitated in the seed crystal phase and are easily produced as fine particles. If calcium fluoride and calcium phosphate are mixed into the treated water And if it is less than 0.8 times, the ratio of fluorine, phosphorus fluoride and calcium phosphate in the raw water is not so high, and fluorine and phosphorus may be mixed into the treated water.
In the present embodiment, seed crystals may be present in the
The seed crystal is not particularly limited as long as it can precipitate crystals of the poorly soluble calcium salt formed on the surface thereof. Any material can be selected, and examples thereof include filtration sand, activated carbon, and zircon sand, garnet sand, Particles composed of an oxide of a metal element such as SAKURUNDUM (trade name, product of Japan Carlit Co., Ltd.), and an insoluble calcium salt as a precipitate by crystallization reaction And the like. However, the present invention is not limited thereto. Particles composed of a poorly soluble salt which is a precipitate by crystallization reaction are preferable from the viewpoint that a more pure poorly soluble salt can be obtained as pellets or the like. Examples of particles composed of a poorly soluble calcium salt as a precipitate by a crystallization reaction include fluorite when calcium fluoride is precipitated and phosphorus ores when calcium phosphate is precipitated .
The flow rate of the raw water passing through the
The flow velocity LV of the treated water flowing through the solid-
Fig. 2 is a schematic diagram showing an example of the constitution of the crystallization reaction apparatus of the reference example. 2 includes a
A raw
In the
The
The upper end of the inner
The
The operation of the
First, raw water containing a substance to be crystallized (hereinafter, sometimes referred to as "raw water") of fluorine and phosphorus is passed through the raw
In the
Crystals of the poorly soluble calcium salt of calcium fluoride and calcium phosphate produced in the
On the other hand, the treated water after the crystallization reaction in the
However, fine particles such as crystals of an insoluble calcium salt that are too fine in particle diameter and can not be precipitated on the seed crystal surface are not separated by the solid-
2, the upper end of the inner
The upper end of the inner
Thus, when the specific gravity difference occurs between the
Next, other conditions of the
The raw water containing the crystallization target in the present embodiment includes fluorine and phosphorus which are removed by crystallization. However, any raw water may be used as long as it includes fluorine and phosphorus. For example, raw water discharged from an electronics industry, a semiconductor industry, a power plant, an aluminum industry, and the like may be used.
Fluorine and phosphorus, which are substances to be crystallized, can be present in the raw water in an arbitrary state if they are crystallized by crystallization reaction. From the viewpoint of being dissolved in the raw water, it is preferable that fluorine and phosphorus are ionized.
In this embodiment, it is preferable that the addition (injection point) of the calcium agent and raw water to the
In the present embodiment, it is preferable to provide the
Further, as described above, when the
Since the crystals having a larger particle diameter due to the crystallization reaction do not rise according to the upward flow of the outer circumferential portion of the tube but sink down and do not enter the
In the present embodiment, the pH of the crystallization reaction solution in the
As the calcium agent used in the present embodiment, for example, calcium chloride, calcium hydroxide and the like are used. The form of adding the calcium agent may be a powder state or a slurry state.
The amount of the calcium agent to be injected is preferably 0.8 to 2 times, and 1 to 2 times, more preferably 1 to 1.2 times as large as the chemical equivalent of calcium. If the chemical equivalent of calcium is more than twice the chemical equivalent of fluorine and phosphorus of the raw water, calcium fluoride and calcium phosphate are not precipitated on the seed crystals but are easily produced as fine particles, and calcium fluoride and calcium phosphate may be mixed into the treated water , The ratio of fluorine in the raw water, calcium fluoride in the phosphorus, and calcium phosphate is increased, so that fluorine and phosphorus may be mixed into the treated water.
In the present embodiment, seed crystals may be present in the
The seed crystal may be any material as long as it can precipitate crystals of the poorly soluble calcium salt formed on the surface thereof. Any material can be selected, and examples thereof include filtration sand, activated carbon and zircon sand, garnet sand, And particles composed of an oxide of a metal element including a metal oxide, and particles composed of a poorly soluble salt as a precipitate due to a crystallization reaction. However, the present invention is not limited thereto. Particles composed of a poorly soluble salt which is a precipitate by crystallization reaction are preferable from the viewpoint that a more pure poorly soluble salt can be obtained as pellets or the like. Examples of the particles composed of a poorly soluble salt as a precipitate by the crystallization reaction include calcium fluoride when calcium fluoride is precipitated and phosphorus ore and the like when calcium phosphate is precipitated .
Example
Hereinafter, the present invention will be described in more detail with reference to examples and comparative examples, but the present invention is not limited to the following examples.
(Example 1)
In Example 1, calcium fluoride was recovered from fluorine-containing raw water under the following conditions by using the crystallization reaction apparatus shown in Fig.
≪
Regular reaction part size: 130ℓ (440mmφ × 880㎜H)
Solid liquid separation size: 230ℓ (440 × 590 × 880㎜H)
<Test Conditions>
Fluorine-containing raw water flow rate: 50 L / h
Fluorine concentration of fluorine-containing raw water: 10000 mg / l
Calcium agent: solution of slaked
PH in the crystallization reaction part: pH 2 (adjusted by adding NaOH)
Initial charge seed crystal in the crystallization reaction part: 20 kg (no seed crystals thereafter)
Slurry concentration in the crystallization reaction part: 30 to 35 v / v% (suitably drawn out from the insoluble salt discharge pipe)
The retention time of the solid-liquid separation portion of Example 1 was 4.6 h (230 (l) / 50 (l / h)), and the retention time of the crystallization reaction portion was 2.6 h.
In Example 1, raw water was passed through the crystallization reaction part for 9.2 hours, and then water was stopped for 2.3 hours. This flow was repeated until the flow time reached 400 hours. The flow rate (LV) of the treated water in the solid-liquid separation portion at the time of water flow was 0.2 m / h. The test was conducted so that a part of the treated water in the solid-liquid separation section was not conveyed to the crystallization reaction section.
(Example 2)
In Example 2, the test was conducted under the same conditions as in Example 1, except that the raw water was passed through the crystallization reaction portion for 4.6 hours and then the water flow was stopped for 1.15 hours.
(Example 3)
In Example 3, the test was carried out under the same conditions as in Example 1, except that the raw water was passed through the crystallization reaction portion for 4.6 hours and then stopped for 2.3 hours.
(Example 4)
In Example 4, a crystallization reaction apparatus in which the solid-liquid separation unit size was changed to 23 liters (440 x 60 x 880 mmH) was used. In Example 4, raw water was passed through the crystallization reaction section for 0.46 hours, and then water was stopped for 0.23 hours. This flow was repeated until the flow time reached 400 hours. The flow rate (LV) of the treated water in the solid-liquid separation portion at the time of water flow was 2.0 m / h.
(Example 5)
In Example 5, the test was carried out under the same conditions as in Example 1, except that raw water was passed through the crystallization reaction portion for 18.4 hours and then stopped for 2.3 hours.
(Comparative Example 1)
In Comparative Example 1, the test was carried out under the same conditions as in Example 1, except that the raw water was not stopped and the raw water was passed through the crystallization reaction portion for 400 hours. The flow rate (LV) of the treated water in the solid-liquid separation portion at the time of water flow was 0.2 m / h.
(Comparative Example 2)
In Comparative Example 2, except that the raw water was passed through the crystallization reaction unit for 400 hours without shutting off the raw water by using a crystallization reaction apparatus in which the solid-liquid separation unit size was changed to 23 liters (440 x 60 x 880 mmH) The test was carried out under the same conditions as in Example 1. The flow rate (LV) of the treated water in the solid-liquid separation portion at the time of water flow was 2.0 m / h.
Table 1 summarizes the flow rates of the treated water in the solid-liquid separation sections of Examples 1 to 5 and Comparative Examples 1 and 2, the flow rate of raw water to the crystallization reaction section, the flow stoppage time, and the recovery rate of calcium fluoride after passage of 400 hours .
(Example 6)
In Example 6, in the crystallization reaction apparatus shown in Fig. 1, a portion of the treated water in the solid-liquid separation portion was returned to the crystallization reaction portion by using a crystallization reaction device in which the upper end of the inner peripheral wall was set at the same height as the treated water outlet The test was carried out under the same conditions as in Example 1. [
(Example 7)
In Example 7, the test was carried out under the same conditions as in Example 6 except that the raw water was passed through the crystallization reaction portion for 4.6 hours and then the water flow was stopped for 2.3 hours.
(Comparative Example 3)
In Comparative Example 3, in the crystallization reaction apparatus shown in Fig. 2, raw water was supplied to the crystallization reaction section without stopping the flow of raw water by using a crystallization reaction device in which the upper end of the inner peripheral wall was set at the same height as the treated water discharge port The test was carried out under the same conditions as in Example 5 except that the water was passed for 400 hours.
Table 2 summarizes the flow rate of the treated water in the solid-liquid separation section of Examples 6 to 7 and Comparative Example 3, the flow rate of raw water to the crystallization reaction section, the flow stoppage time, and the recovery rate of calcium fluoride after 400 hours of passage.
FIG. 3 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Example 1. FIG. 4 is a diagram showing a particle diameter distribution of crystals in the crystallization reaction section of Example 2. FIG. FIG. 6 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Example 4, and FIG. 7 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Comparative Example 1 Fig. 8 is a graph showing the particle diameter distribution of crystals in the crystallization reaction section of Comparative Example 2, and Fig. 9 is a diagram showing the particle diameter distribution of crystals in the crystallization reaction portion of Comparative Example 3. Fig. The particle diameter distribution of crystals in the crystallization reaction section was measured using a particle size distribution analyzer (LS230 manufactured by Beckman Coulter Inc.) after 400 hours of water flow in the crystallization reaction section.
In Comparative Example 1 in which calcium fluoride was recovered by continuous feed of raw water without replenishing seed crystals, as can be seen from the results of Fig. 7 and Table 1, crystals having a particle diameter of 100 탆 or more And the recovery rate was as low as 65%. In Comparative Example 2 in which the flow rate of the treated water in the solid-liquid separation portion was increased to 2.0 m / h, as can be seen from the results in Fig. 8 and Table 1, crystals having a particle diameter of 125 탆 or more , And the recovery rate was further lowered to 50%. On the other hand, in the embodiment in which the feed water of the raw water is intermittently performed, specifically, the feed water of the raw water is performed for 1/2 time or more and 5 times or less of the residence time of the solid- As can be seen from the results of Figs. 3 to 6 and Table 1, in Examples 1 to 5 in which the time was more than 1 time and not more than 1 time, many crystals having a particle diameter of 100 탆 or less existed in the crystallization reaction portion, 75% or more, and a higher recovery than Comparative Examples 1 and 2 was obtained. Particularly, Example 3 in which the feed water of the raw water was performed for one time of the residence time of the solid-liquid separation portion, and for stopping the flow of water for a time of ½ times the residence time of the solid-liquid separation portion, 5 and 6, and Table 1, it was confirmed that particles having a particle diameter of 50 mu m or less and a particle diameter of 50 mu m or less And a recovery rate higher than that of Examples 1 and 2 was obtained at a recovery rate of 90% or more. That is, the flow of the raw water is performed for a period of time that is one time of the residence time of the solid-liquid separation section, and the flow stopping is performed for a period of time equal to 1/2 of the residence time of the solid-liquid separation section, And the recovery rate of calcium fluoride crystals was also improved.
As can be seen from the results in Table 2, in Examples 6 and 7, the raw water was intermittently circulated, and a part of the treated water in the solid-liquid separation portion was returned to the crystallization reaction portion beyond the inner peripheral wall, %. ≪ / RTI >
1, 100:
12, 112:
16, 116: raw
20, 118: seed
22, 120: treated
26, 124: inner
30, 128: solid-
34, 132:
38, 138: stirring wing
Claims (4)
And a circulation reaction unit having a crystallization reaction unit for adding crystals to the raw water containing fluorine to generate crystals of the insoluble salt, and a circulation means for passing the raw water to the crystallization reaction unit,
An inner peripheral wall opposite to the outer peripheral wall of the crystallization reaction vessel is disposed in the crystallization reaction vessel and an upward flow is formed between the inner peripheral wall and the outer peripheral wall to form a solid- And,
Wherein said water passing means intermittently feeds said raw water to said crystallization reaction section,
The water-passing time and the water-stop time by the water-passing means are set based on the residence time of the raw water in the solid-liquid separator (the volume of the solid-liquid separator / the inflow of the raw water into the crystallization reactor)
Wherein the water supply time of the raw water at the time of intermittent passing by the water passing means is not less than 1/2 times and not more than 5 times the residence time of the solid-liquid separating portion, And the time is a time that is one fifth or more and one time or less of the residence time in the solid-liquid separation unit.
An outlet for discharging the treated water is formed on an outer peripheral wall of the crystallization reaction tank provided with the solid-liquid separation unit,
The upper end of the inner peripheral wall is at the same height as the discharge port or at a position lower than the discharge port within a range in which a part of the treated water can be discharged from the discharge port and a part of the treated water in the solid- And is conveyed to the crystallization reaction section.
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PCT/JP2013/067526 WO2014207837A1 (en) | 2013-06-26 | 2013-06-26 | Crystallization reactor |
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KR101793809B1 true KR101793809B1 (en) | 2017-11-03 |
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CN (1) | CN105339063B (en) |
SG (1) | SG11201509658PA (en) |
WO (1) | WO2014207837A1 (en) |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001038370A (en) * | 1999-08-03 | 2001-02-13 | Maezawa Ind Inc | Waste water treatment device |
JP2002292204A (en) * | 2001-03-30 | 2002-10-08 | Japan Organo Co Ltd | Crystallization reaction apparatus provided with means for controlling amount of raw water to be supplied and crystallization method to use the same |
JP2004321992A (en) * | 2003-04-25 | 2004-11-18 | Ataka Construction & Engineering Co Ltd | Phosphorus resource recovery apparatus |
Family Cites Families (4)
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JPS61141996A (en) * | 1984-12-17 | 1986-06-28 | Ataka Kogyo Kk | Treatment of waste water |
JP4842450B2 (en) * | 2001-03-30 | 2011-12-21 | オルガノ株式会社 | Crystallization reactor equipped with turbidity measuring means and crystallization treatment method using the same |
JP4316393B2 (en) * | 2004-01-21 | 2009-08-19 | 森田化学工業株式会社 | Calcium fluoride manufacturing method, recycling method and recycling method |
JP5414169B2 (en) * | 2007-11-15 | 2014-02-12 | オルガノ株式会社 | Crystallization reactor and crystallization reaction method |
-
2013
- 2013-06-26 KR KR1020157033811A patent/KR101793809B1/en active IP Right Grant
- 2013-06-26 WO PCT/JP2013/067526 patent/WO2014207837A1/en active Application Filing
- 2013-06-26 CN CN201380077825.7A patent/CN105339063B/en active Active
- 2013-06-26 SG SG11201509658PA patent/SG11201509658PA/en unknown
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001038370A (en) * | 1999-08-03 | 2001-02-13 | Maezawa Ind Inc | Waste water treatment device |
JP2002292204A (en) * | 2001-03-30 | 2002-10-08 | Japan Organo Co Ltd | Crystallization reaction apparatus provided with means for controlling amount of raw water to be supplied and crystallization method to use the same |
JP2004321992A (en) * | 2003-04-25 | 2004-11-18 | Ataka Construction & Engineering Co Ltd | Phosphorus resource recovery apparatus |
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KR20160004361A (en) | 2016-01-12 |
SG11201509658PA (en) | 2015-12-30 |
CN105339063B (en) | 2017-03-08 |
CN105339063A (en) | 2016-02-17 |
WO2014207837A1 (en) | 2014-12-31 |
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