CN1403373A - Sulfate radical-eliminating process for underground bittern - Google Patents

Sulfate radical-eliminating process for underground bittern Download PDF

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Publication number
CN1403373A
CN1403373A CN 02138308 CN02138308A CN1403373A CN 1403373 A CN1403373 A CN 1403373A CN 02138308 CN02138308 CN 02138308 CN 02138308 A CN02138308 A CN 02138308A CN 1403373 A CN1403373 A CN 1403373A
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brine
square
reactor
waste liquid
filter
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CN1193934C (en
Inventor
张国兴
赵根庆
汪春茂
邢亚琴
王炳辉
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Lianyungang Alkali Plant Of Sinopec Nanjing Chemical Industry Co ltd
NANHUA GROUP DESIGN INST
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DESIGN INST OF NANJING CHEMICAL GROUP Co
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Abstract

The present invention is the sulfate radical eliminating process for underground bittern. Calcium chloride contained in the distilled waste liquid from ammonia alkali process to produce sodium carbonate is made to react with sulfate radical in bittern with the molar ratio between Ca ion and sulfate radical ion being 1.5-1.7. Special multiple-checker square tank reactor is adopted to prolong the effective chemical reaction time for full reaction; the solid material is made to float to avoid deposit; and the suspended material is separated via membrane filtering process. The separated brine product has sulfate radical content less 2 g/L and solid content less than 1 mg/L and may be used as material for ammonia alkali process to produce sodium carbonate.

Description

Method for removing sulfate radical from underground brine
The invention relates to a method for removing sulfate radical from underground brine used as a raw material for preparing soda ash by an ammonia-soda process, belonging to the field of soda ash industry.
[ II]background of the invention
The ammonia-soda process for producing soda ash is characterized by that the saturated salt water, lime and NH are mixed3、CO2Sodium carbonate product is generated by reaction and CaCl is discharged2OfThe distillation waste liquid requires that the sulfate ion in the raw material brine is controlled within 2.0 g/l. At present, most of domestic soda ash enterprises adopt solid sea salt as a raw material, and the sulfate radical content generally can meet the production requirement, so that the removal of sulfate radicals is not needed, but the production cost is higher. The cheap underground brine is adopted to replace sea salt as the raw material of the soda ash, so that the production cost of the soda ash can be reduced, and the problem of supply and demand contradiction caused by the influence of seasons on the yield of the sea salt can be solved. Because underground brine extracted by water solution in China contains 5-60 g/l of sodium sulfate, if the underground brine is directly used for soda production, the evaporation and absorption process can be seriously scaled, so that the production cannot be normally carried out, the underground brine needs to be removed before entering a soda production device, and the key of removing sulfate radicals by an economical and reliable method is related to whether the underground brine can become a soda production raw material.
Method for removing SO from brine by chemical method4 2-Generally, there are two methods, chemical calcium method and chemical barium method, and the chemical reaction formula is as follows: a) chemical calcium method: b) chemical barium method:
BaSO produced by the latter barium method4The reaction process is complete for insoluble matters, and equimolar Ba is adopted2+The reaction can achieve the purpose of removing SO4 2-And (4) requiring. CaSO generated by the calcium method of the former4·2H2O is slightly soluble, equimolar Ca2+Only SO in brine can be ensured4 2-Except that the amount of SO is 3.5-4.0 g/l4 2-The Ca content in the reaction solution must be maintained below 2g/l required by soda production2+In excess. Theoretically, Ca2+With SO4 2-When the molar ratio (hypercalcemia ratio for short) of (1.4), SO of the brine after reaction can be ensured4 2-The calcium content is reduced to below 2g/l, and the calcium content ratio is generally required to be controlled to be above 1.7-2.0 in the conventional reaction and sedimentation separation process of industrial production.
However, since BaCl2·2H2The price of the O raw material is far higher than that of CaCl2Therefore, the barium process is much more costly than the calcium process, and BaCl2Is toxic. In contrast, it is not necessary to provide a separate control unitCalcium method for removing SO4 2-Not only the raw material cost is low, but also the usable gypsum byproduct CaSO can be generated4·2H2O。
The traditional method for removing sulfate radicals in brine by calcium chloride is to dissolve solid calcium chloride in water, then reactthe solid calcium chloride with brine in a circular tank connected in series, and then separate the solid calcium chloride by settling sand filtration, so as to improve the effects of mixed reaction and solid-liquid separation, a very huge circular tank reactor and a huge clarifying barrel need to be designed to ensure longer reaction time and settling time, but the CaSO4·2H2O is in suspension state in the material, the sedimentation is very slow, the separation efficiency is low, even if a huge clarifying barrel is adopted, the solid-liquid separation is still difficult to be complete, the quality of clear liquid is very unstable, and CaSO4·2H2O is easy to scale in equipment and pipelines and difficult to clean. Because the reaction and the solid-liquid separation are difficult to be completed, the unreacted SO4 2-And unseparated clean CaSO4·2H2O remains in the brine for further subsequent Ca removal2+In the treatment, CaSO4·2H2O is easily dissolved back to SO4 2-And (4) ions are used for increasing the concentration of sulfate radicals in the brine. To make SO4 2-When the standard is reached, SO must be removed4 2-The calcium ratio is controlled to be higher during the reaction, and the surplus Ca is treated2+And the cost is increased due to the consumption of soda ash.
[ III]summary of the invention
The invention aims to provide a novel method for removing sulfate radicals from underground brine, which aims to reduce the calcium passing ratio of chemical reaction, improve the chemical reaction efficiency and the separation effect of suspended materials, realize high removal rate of sulfate radicals and obtain low-price and high-quality production raw materials in the soda industry.
As is known to all, the distillation waste liquid in the ammonia-soda process soda ash production contains a large amount of calcium chloride, and the invention utilizes the supernatant liquid after the ammonia-soda distillation waste liquid is clarified or the waste clear liquid after beach drying (hereinafter referred to as distillation waste liquid) as CaCl required by underground brine for removing sulfate radical2Of the raw material source of (1), CaCl thereof2Content (wt.)8 to 20 percent (wt).
The method for removing sulfate radical from underground brine comprises the following steps: a) according to SO in brine4 2-And Ca in the raw distillation waste liquid2+Measuring the concentration value, calculating the Ca value2+With SO4 2-The weight flow ratio n of the distillation waste liquid to the brine with the molar ratio of 1.5-1.7; b) respectively pumping the distilled waste liquid and the brine into a multi-grid square groove reactor for stirring and mixing, adjusting the flow rate of the distilled waste liquid and the brine to enable the flow rate ratio to meet n, controlling the reaction time of the materials in the groove to be 40-60 minutes, and combining impurity ions in the materials to generate solid suspended matters. In the process, Na in brine2SO4With CaCl in the distillation waste liquid2A chemical reaction takes place, SO4 2-With Ca2+Reaction to form CaSO4·2H2O solid suspended matter and NaCl as effective component.
c) From the outlet of the multi-grid square tank reactor, the reactor contains CaSO4·2H2Pumping the material of the O solid suspended matter into a membrane filter for solid-liquid separation, allowing clear liquid to flow out after permeating membrane pores, collecting saline water without sulfate radical, and allowing the solid-containing material which does not permeate the membrane to remain in the filter and be discharged from the bottom of the filter; the membrane aperture of the membrane filter is 0.5-1.5 microns, and the pressure of the membrane filter during filtration is 0.02-0.3 MPa.
d) Pumping the gypsum salt slurry discharged from the bottom of the filter into a filter press for gypsum drying treatment, wherein the solid phase material is a gypsum product, and the liquid phase containing NaCl is recycled and returned to the reactor for re-separation.
In conclusion, the invention adopts a specially designed multi-grid reactor, materials can keep longer effective reaction time in the reactor, and Na in brine is ensured2SO4Sufficiently converting the reaction slurry into solid suspended matter by using a membrane filter, and separating solid particles (CaSO) by using the nanofiltration characteristic of the membrane4·2H2O and solid suspended matters) are thoroughly separated from the solution, the removal rate of the solid reaches 99.9 percent, the quality of the filtered clear liquid is easy to ensure, and compared with the traditional sedimentation separation method, the occupied area of the filter is very smallThe area is small, the separation efficiency and the separation quality are greatly improved, SO that the SO required by the brine serving as the raw material for producing the calcined soda in the filtered clear brine is achieved4 2-The index of less than or equal to 2g/l and the solid content of less than or equal to 1 mg/l. Therefore, the method can achieve the full reaction and the full separation of solid-liquid materials, thereby the quality of the refined brine is high. In addition, the invention further reduces the cost of removing sulfate radicals from brine by using the waste distillation waste liquid generated in the production of soda ash as the raw material, thereby reducing CaCl in the distillation waste liquid2The pollution is discharged, the effective component NaCl is generated, and the NaCl in the waste liquid is recycled.
The invention designs a special multi-grid square groove reactor for the chemical reaction, and aims to prolong the effective reaction time of materials in the reactor and facilitate the reaction to CaSO4·2H2The generation of O and the scale formation of products in the device are avoided, so that the addition of the distillation waste liquid is effectively controlled, the consumption of soda ash is reduced, and the cost is reduced.
The multi-grid square groove reactor provided by the invention is provided with a material inlet and a material outlet, the groove of the reactor is divided into a plurality of square reaction areas, each grid is internally provided with a stirrer, the partition plates of two adjacent grids in the material flowing direction are provided with material overflow ports, a flow guide hopper with a wide upper part and a narrow lower part is arranged above the overflow ports in the front grid of the partition plate, a flow guide groove extending downwards from the overflow ports is arranged in the rear grid of the partition plate, the flow guide hopper in the front grid and the flow guide groove in the rear grid are respectively arranged on two sides of the same partition plate, and the two flow guide hoppers are communicated with each other at the material overflow ports. In addition, the reaction tank of the invention also comprises the following characteristics:
four corners of each square reaction area are provided with baffles in opposite angle directions, so that dead angles of materials are avoided. The blade surface of the stirrer is an arc transition twisted surface with gradually narrowed width, and the edge of the blade is also in an arc transition curve; the stirrer is fixed through the frame.
In the reactor, the reaction mass passes through the compartments in the tank in a predetermined flow direction until it finally flows out of the reactor. The diversion hopper, the material through hole and the diversion trench are used for feeding materials from the lower part and discharging materials from the upper part of each reaction area, so that the retention time in the material areas is prolonged, and the full reaction is ensured.Because of the special structure of the stirrer blade of the reactor, the stirrer can fully stir materials in the reaction zone, so that the materials can fully react, and simultaneously, the generated crystal can be kept in a suspended state without being crushed, thereby preventing deposition. The baffle plate can prevent dead angles and blind areas, and has the function of changing the flow direction of the materials, so that the materials react more fully. Therefore, the multi-grid square-groove reactor can realize enough material residence time in the reactor under the condition of smaller reaction volume and occupied area, and ensure SO4 2-With Ca2+Sufficiently combines and effectively prevents fouling, thereby making the reaction low in Ca2+/SO4 2-Implementation of the molar ratio scheme, SO4 2-Can be reduced to 1g/l or even lower, and the residual Ca in the materials after the reaction2+The content is reduced to 3.5-4.0 g/l, and the residual Ca is saved2+The cost of the process.
(IV) description of the drawings
FIG. 1 is a process flow diagram for the removal of sulfate from an underground brine in accordance with the present invention.
FIG. 2 is a schematicview showing the structure of a multi-cell reactor for sulfate removal reaction according to the present invention, and FIG. 3 is a plan view of FIG. 2. FIG. 4 is a perspective view of one blade of the agitator.
The technological process for removing sulfate radical in the brine is shown in figure 1. Raw brine is sent into a multi-grid square groove reactor 4 from a raw brine storage tank 1 through a raw brine pump 3, distilled waste liquid from the storage tank 2 is sent into the reactor 4 through a raw brine pump 3' to be stirred and mixed with the raw brine, materials after reaction are sent into a membrane filter 6 from an outlet of the reactor 4 through a material pump 5, the materials are filtered and separated through a porous organic membrane in the reactor, solid suspended matters in the materials are blocked outside the membrane, clear liquid is discharged from the top of the filter through membrane holes and flows into a brine storage tank 10, and the clear liquid is sent to a brine refining system of a soda device through a brine pump 11 to be used as a raw material for producing soda. Most of the suspended matters which are not permeated by the filter are settled and discharged from the bottom of the filter, the suspended matters are sent to a salt mud filter press by a pump 8 to remove the brine in the salt mud filter press to obtain a gypsum byproduct, and the brine separated by the filter pressing is returned to the reactor 4 to participate in the re-separation. With the progress of the filtration process, the amount of solids adhering to the surface of the porous membrane increases, and when the separation efficiency decreases to a certain extent, the automatic control system controls the pump 5 to stop the pump, the overflow clear liquid in the filter 6 temporarily stops outputting, and the liquid level automatically drops and flows back to the reactor 4 through the pipem. In the process, the solid on the surface of the membrane falls off due to the recoil action of the saline water and sinks into the bottom of the filter by gravity, so that the membrane surface is cleaned, and the next filtration is started again. The operation of the filter is kept under high flow and low filtration resistance by the circulation.
As can be seen from FIGS. 2 and 3, the square groove 18 of the multi-compartment reactor is divided into a plurality of reaction zones in the form of lattices by partition plates 13, in this example four reaction zones are divided, and the raw material is fed from zone A, passed through B, C, D in sequence, and finally discharged through outlet pipe 16. The division plates between the intervals A, B, B, C, C and D are respectively provided with a flow guide device 21 which comprises a flow guide hopper 21-1 and a flow guide groove 21-2, wherein the flow guide hopper 21-1 and the flow guide groove 21-2 are respectively arranged at the front side and the rear side of the same division plate and are respectively positioned at the upper side and the lower side of an overflow port 22 (see figure 2); fig. 2 shows that the diversion hopper 21-1 is in a hopper shape with a wide top and a narrow bottom, and the diversion trench 21-2 extends downwards from the overflow port 22 and is communicated with the overflow port 22. The flow sequence of the materials in each grid of the reactor can be designed according to the needs, the feeding grid and the discharging grid can be selected at will, only one of the four discharging ports 16 in the figure 2 is actually selected, and the rest of the four discharging ports are closed when not used. Fig. 3 shows that each reaction zone is provided with diagonally oriented baffles 15 at the four corners of the grid, which prevent dead spots of material. The stirrer 20 is fixed by a frame 14 arranged above the reactor, the shape of a stirrer blade 20-1 is shown in figure 4, the blade surface of the stirrer blade is a twisted surface with gradually narrowed width and arc transition, and the edge of the blade is an arc transition curve. The arrows in FIG. 2 indicate the change in the flow of material from reaction zone B to reaction zone C. The material in the B area after the stirring reaction passes through the diversion hopper 21-1 from the upper part and enters the lower part of the C area downwards along the diversion trench 21-2 through the overflow port 22, and then is continuously reacted after additional stirring and then is guided upwards into the next reaction area through the diversion device. Therefore, the materials are in curved three-dimensional tumbling flow in the reactor, so that the effective reaction residence time is prolonged, and the reaction is more complete. The special structure of the stirrer can not only fully mix the materials, but also ensure that coarse crystals of solid products are not damaged and the suspension state of the crystals can be kept, thereby effectively preventing deposition and scaling and creating conditions for the subsequent separation process.
Detailed description of the preferred embodiments
Example 1:
9.36g/l sulfate radical and 290g/l sodium chloride containing underground brine of Huaiyin in China and CaCl are added into a six-grid square tank reactor212.5 percent ammonia-soda distillation waste liquid, the reaction temperature is 31 ℃, the adding proportion is that the weight flow ratio n of the distillation waste liquid and the brine is 0.13, after stirring and reacting for 50 minutes, a pump is used for pumping into a polytetrafluoroethylene film filter with the film aperture of 0.8 mu m for filtering, and the filtering pressure is 0.18 Mpa. Using EDTA back titration method to filter the refined brine; determination of SO4 2-Content, turbidity (SS) by FAU turbidimetry, Ca by EDTA titration2+;SO4 2-1.64g/l, no SS detected, Ca2+It was 3.65 g/l. SO (SO)4 2The SS content completely meets the requirement of producing soda by ammonia-soda processAnd (6) obtaining.
Example 2
Adding 15.36g/l sulfate radical-containing and 285g/l sodium chloride underground Huaian brine into a six-grid square tank reactor, and simultaneously adding CaCl-containing underground brine according to a proportion28 percent of ammonia-soda distillation waste liquid, the reaction temperature is 24 ℃, the adding proportion is that the weight flow ratio n of the distillation waste liquid and the brine is 0.23, after stirring and reacting for 45 minutes, a pump is used for pumping into a polytetrafluoroethylene film filter with the film aperture of 0.10 mu m for filtering, and the filtering pressure is 0.15 Mpa. Filtering with a membrane filter, and measuring SO in the filtered refined brine by EDTA back titration4 2-Turbidity (SS) by FAU specific etching and Ca by EDTA titration2+As a result of SO4 2-1.52g/l, turbidity 0.16mg/l, Ca2+It was 3.84 g/l. SO (SO)4 2-And SS can meet the production requirements of soda ash by an ammonia-soda process.

Claims (6)

1. The method for removing sulfate radical from underground brine is characterized in that distillation waste liquid produced by soda ash by an ammonia-soda process is used as a raw material, and comprises the following steps:
a. according to SO in brine4 2-And Ca in the raw distillation waste liquid2+Measuring the concentration value, calculating the Ca value2+With SO4 2-The weight flow ratio n ofthe distillation waste liquid to the brine with the molar ratio of 1.5-1.7;
b. respectively pumping the distilled waste liquid and the brine into a multi-grid square groove reactor for stirring and mixing, adjusting the flow rate of the distilled waste liquid and the brine to enable the flow rate ratio to meet n, controlling the reaction time of the materials in the groove to be 40-60 minutes, and enabling impurity ions in the materials to generate solid suspended matters.
c. From the outlet of the multi-grid square tank reactor, the reactor contains CaSO4·2H2And pumping the material of the O solid suspended matter into a membrane filter for solid-liquid separation, wherein clear liquid flows out after permeating membrane holes, collecting the saline water without sulfate radicals, and settling the material which does not permeate the membrane at the bottom of the filter for discharge.
d. Pumping the solid suspended matter discharged from the bottom of the membrane filter into a filter press for further filter pressing, recovering the separated NaCl-containing liquid phase to the reactor for re-separation, wherein the fixed material is a gypsum byproduct.
2. The process of removing sulfate from underground brine according to claim 1, wherein the membrane filtration in step c has a pore size of 0.5 to 1.5 μm.
3. A process for the removal of sulfate from underground brine according to claim 1 or 2, wherein the membrane filter in step c has a filtration pressure of 0.02 to 0.3 Mpa.
4. A multi-grid square-tank reactor special for the method of claim 1, which has a material inlet and a material outlet, and is characterized in that the interior of the reactoris divided into a plurality of square-shaped reaction zones by partition plates, each square-shaped reaction zone is provided with a stirrer, the partition plates of two adjacent squares arranged according to the material flow program are provided with material through holes, the front square of each partition plate is provided with a flow guide hopper which is gradually widened upwards from the material through holes, the rear square of each partition plate is provided with flow guide grooves which extend downwards from the material through holes, and the flow guide hopper and the flow guide grooves are respectively arranged on two sides of each partition plate and are communicated with each other at the material through.
5. A multi-cell square tub reactor according to claim 4, wherein each of the four corners of each of the square-shaped reaction zones is provided with a baffle plate in a diagonal direction.
6. A multi-cell square tank reactor as claimed in claim 4 or 5, wherein the agitator has a twisted surface with a narrowing width and an arc transition, and the edge of the blade is curved with an arc transition.
CNB021383081A 2002-09-20 2002-09-20 Sulfate radical-eliminating process for underground bittern Expired - Fee Related CN1193934C (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100358623C (en) * 2005-04-07 2008-01-02 凯膜过滤技术(上海)有限公司 Homogeneous-phase fluidized bed reactor
CN102153127A (en) * 2011-03-12 2011-08-17 广东南方碱业股份有限公司 Method for preparing gypsum by removing sulfate radicals from mineral salts with waste distillation liquid from ammonia alkali factory
CN102190319A (en) * 2010-03-15 2011-09-21 大连化工研究设计院 Novel process for refining brine
CN104891704A (en) * 2015-05-05 2015-09-09 岳嵩 High-salt content waste water treatment method
CN105905927A (en) * 2016-06-20 2016-08-31 中盐金坛盐化有限责任公司 Brine purification device and method for removing strontium element from sodium sulfate type brine

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102951668B (en) * 2012-12-13 2014-09-03 国家海洋局天津海水淡化与综合利用研究所 Method for co-producing calcium sulphate and magnesium hydrate by ammonia alkali waste liquid and concentrated seawater

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100358623C (en) * 2005-04-07 2008-01-02 凯膜过滤技术(上海)有限公司 Homogeneous-phase fluidized bed reactor
CN102190319A (en) * 2010-03-15 2011-09-21 大连化工研究设计院 Novel process for refining brine
CN102190319B (en) * 2010-03-15 2013-01-30 中昊(大连)化工研究设计院有限公司 Novel process for refining brine
CN102153127A (en) * 2011-03-12 2011-08-17 广东南方碱业股份有限公司 Method for preparing gypsum by removing sulfate radicals from mineral salts with waste distillation liquid from ammonia alkali factory
CN102153127B (en) * 2011-03-12 2013-06-19 广东南方碱业股份有限公司 Method for preparing gypsum by removing sulfate radicals from mineral salts with waste distillation liquid from ammonia alkali factory
CN104891704A (en) * 2015-05-05 2015-09-09 岳嵩 High-salt content waste water treatment method
CN105905927A (en) * 2016-06-20 2016-08-31 中盐金坛盐化有限责任公司 Brine purification device and method for removing strontium element from sodium sulfate type brine

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