CN102642963A - Comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal - Google Patents

Comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal Download PDF

Info

Publication number
CN102642963A
CN102642963A CN2012101103133A CN201210110313A CN102642963A CN 102642963 A CN102642963 A CN 102642963A CN 2012101103133 A CN2012101103133 A CN 2012101103133A CN 201210110313 A CN201210110313 A CN 201210110313A CN 102642963 A CN102642963 A CN 102642963A
Authority
CN
China
Prior art keywords
water
stone coal
salt
extracting vanadium
brine
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN2012101103133A
Other languages
Chinese (zh)
Other versions
CN102642963B (en
Inventor
包申旭
张一敏
黄伟
刘涛
陈铁军
黄晶
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Wuhan University of Technology WUT
Original Assignee
Wuhan University of Technology WUT
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Wuhan University of Technology WUT filed Critical Wuhan University of Technology WUT
Priority to CN201210110313.3A priority Critical patent/CN102642963B/en
Publication of CN102642963A publication Critical patent/CN102642963A/en
Application granted granted Critical
Publication of CN102642963B publication Critical patent/CN102642963B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Water Treatment By Electricity Or Magnetism (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The invention relates to a comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal. The invention adopts the technical scheme that: firstly pre-treating the salt-contained waste water until the following conditions are satisfied: iron ion (Fe<2+>) is less than 0.3mg/L, manganese ion (Mn<2+>) is less than 0.1mg/L, and SS is less than 1mg/L; carrying out desalting treatment by utilizing reversed-electrode electrodialysis, concentrating the salt-contained waste water to 100000 to 120000mg/L, and recycling fresh water for a stone-coal vanadium extraction process; carrying out the concentration treatment by adopting a vacuum membrane distillation way, acquiring saturated salt water and condensed water, recycling the condensed water for the stone-coal vanadium extraction process, and feeding the saturated salt water into a concentrated water pool; finally carrying out the crystallization in a crystallization chamber which is previously filled with sodium chloride (NaCl), drying the crystallized salt in the sun to acquire the industrial salt, and returning the acquired industrial salt to the stone-coal vanadium extraction process; and filtering and returning the crystallization liquid to the concentrated water pool to be returned to the vacuum membrane distillation process after being mixed and heated with the concentrated water produced by the electrodialysis. According to the comprehensive treatment method, the energy consumption is small, fresh water and salt in the waste water can be completely recycled, comprehensive utilization of the waste water is realized, no secondary pollution occurs to the environment, and the treatment cost is low.

Description

A kind of integrated conduct method of extracting vanadium from stone coal brine waste
Technical field
The invention belongs to brine waste and handle and the comprehensive utilization field, relate in particular to a kind of integrated conduct method of extracting vanadium from stone coal brine waste.
Background technology
Along with vanadium in extensive applications such as iron and steel, chemical industry, aerospace, the consumption of vanadium constantly increases.China is as one of abundant country of vanadium resource, become gradually vanadium market, the world strong rival (Wang Yongshuan etc., China's extracting vanadium from stone coal and comprehensive utilization summary " vanadium titanium " 1993,4:21-31).Bone coal is a kind of important vanadium resource that contains of China, has big, the characteristics such as extensive that distribute of reserves, and therefore vanadium extraction is to satisfy the important channel of vanadium demand from now on from bone coal.In the stone coal vanadium-extracting roasting process, need to add certain amount of industrial salt promotes vanadium as roasting additive extraction usually; Very high (the Yi-Min Zhang of saltiness that causes vanadium extracting waste water; Et al.The technology of extracting Vanadium from stone coal in China:History; Current status and future prospects. " Hydrometallurgy " 2011,109:116~124).This brine waste can etching apparatus, if not treatedly directly efflux, can cause the soil compaction of discharge areas, and farm crop are impaired, water body salinization, influence ecological environment.So, must handle this type of brine waste, realize the comprehensive utilization of waste water simultaneously, reduce production costs.
Brine waste is carried out desalting treatment, and the harmless emission of realizing such water body is one of current environmental protection field urgent problem.Current; Generally adopt metallic reducing-lime neutralisation to handle for the extracting vanadium from stone coal brine waste, this method technical process is simple, can remove most of deleterious heavy metal ion (Ceng Fanyong in the waste water; " engineering design and research (Changsha) " 1996 is inquired in the wastewater treatment of acid system extracting vanadium from stone coal; 3:62-64), but still there is the salt concn problem of higher in the waste water after handling, needs further to handle.
When the technology of pre-treatment brine waste has multi-effect distilling and membrane method treating process: multi-effect distilling can concentrate saline solns dramatically; But because the service temperature of waste water is near 100 ℃, energy expenditure is very big, the perishable (Yu Kailu etc. of equipment; Low temperature multiple-effect distillation sea water desalting engineering and technical progress " Chinese water supply and drainage " 2008; 24:82-85), exist facility investment huge simultaneously, the very high shortcoming of processing cost; Membrane method treating process has r-o-and electrodialysis, owing to need not waste water is heated to comparatively high temps in the treating processes, has reduced energy consumption; But membrane method treating process is had relatively high expectations to pre-treatment, and film pollutes easily, and (Chu Yanjie etc., reverse osmosis membrane pollute and in face distribution characteristics research " water technology " 2012; 38:72-74; 133), owing to receive the restriction of film properties, concentrating degree is limited simultaneously; And high strong brine discharging (Zhao Shigang etc., discussion " process water and waste water that reverse osmosis concentrated water is recycled of some secondary still after handling; Li Guang etc., the development of electrodialytic technique and application " chemical technology and exploitation " 2008 37:28-30), can cause second environmental pollution.
Summary of the invention
The present invention is intended to overcome the defective of prior art, purpose provides that a kind of energy expenditure is less, processing cost is lower, to the environment non-secondary pollution, can all reclaim the wherein integrated conduct method of the extracting vanadium from stone coal brine waste of fresh water and salt.
For realizing above-mentioned purpose, the concrete steps of the technical scheme that the present invention adopts are:
The first step, pre-treatment
Adopt lime neutralization-soda ash to remove hard-flocculent precipitation, with the pre-treatment of extracting vanadium from stone coal brine waste extremely: Fe 2+<0.3mg/L, Mn 2+<0.1mg/L, SS<1mg/L.
Second step, pole-reversing electroosmosis
Adopt pole-reversing electroosmosis that pretreated extracting vanadium from stone coal brine waste is carried out desalting treatment; Per 2~2.5 hours reverses once in the desalting treatment process; Extracting vanadium from stone coal brine waste salinity after pole-reversing electroosmosis is handled is concentrated into 100000~120000mg/L; Obtain fresh water and dense water, wherein fresh water is back to process for extracting vanadium from stone coal.
The 3rd step, pressure reducing film distillation
The dense water that adopts pressure reducing film distillation technology that second step was obtained carries out concentration, and per-meate side vacuum tightness is 90~95kPa in the concentration process, obtains saturated brine and water of condensation, and water of condensation is back to process for extracting vanadium from stone coal, and saturated brine gets into dense pond.
The 4th step, crystallization
Crystallization be with crystallisation chamber that dense pond communicates in carry out, be added with solid NaCl in the crystallisation chamber in advance; The saturated brine that gets into crystallisation chamber from dense pond is in the crystallisation chamber crystallization, and the crystal salt after the crystallization makes Industrial Salt through evaporating brine, and the gained Industrial Salt returns process for extracting vanadium from stone coal; Crystal solution is returned dense pond through filtration, the dense hydration that the supernatant in dense pond and electrodialysis are produced also, the supernatant after the merging and dense water return the 3rd pressure reducing film distillation technology that goes on foot after heating.
Total salinity of said extracting vanadium from stone coal brine waste is 10000~35000mg/L.
The thermal source of said heating is an industrial waste heat, and heated temperatures is 55~75 ℃.
Used membrane distillation assembly adopts tubular fibre formula membrane module in the described pressure reducing film distillation, and the filling ratio of tubular fibre formula membrane module is 30%~60%, and length-to-diameter ratio is (3~6): 1; The material of tubular fibre formula membrane module is hydrophobicity pvdf or hydrophobicity tetrafluoroethylene, and mean pore size is 0.2 μ m.
Because adopt technique scheme, heating thermal source of the present invention is an industrial waste heat, and only need the extracting vanadium from stone coal brine waste is heated to 55~75 ℃, when the preparation Industrial Salt, adopt the technology of evaporating brine, so energy expenditure is less; In the comprehensive treating process process, can all reclaim wherein fresh water and salt, the final product direct reuse has been realized the comprehensive utilization of waste water in process for extracting vanadium from stone coal, and to the environment non-secondary pollution, processing cost is low.
The present invention also has the technology flexible characteristic, both can be used for the comprehensive treating process of extracting vanadium from stone coal brine waste, also can be used for other industry and goes up the processing of brine waste, brackish water desalination processing and sea water desaltination processing.
Description of drawings
Fig. 1 is a kind of process flow diagram of the present invention.
Embodiment
Below in conjunction with accompanying drawing and embodiment the present invention being further described, is not the restriction to its protection domain:
For avoiding repetition, the chemical ingredients that earlier this embodiment institute will be carried out the extracting vanadium from stone coal brine waste of comprehensive treating process is described below, and repeat no more among the embodiment: always salinity is 10000~35000mg/L, Ca 2+Be 300~650mg/L, Mg 2+Be 60~300mg/L, SS (suspended solid) is 400~750mg/L; Main heavy metal ion is: Zn 2+Be 45~75mg/L, Fe 2+Be 30~50mg/L, Cu 2+Be 10~30mg/L, Mn 2+Be 0.5~4mg/L.
Embodiment 1
A kind of integrated conduct method of extracting vanadium from stone coal brine waste.The concrete steps of its treatment process are as shown in Figure 1:
The first step, pre-treatment
Adopt lime neutralization-soda ash to remove hard-flocculent precipitation, with the pre-treatment of extracting vanadium from stone coal brine waste extremely: Fe 2+<0.3mg/L, Mn 2+<0.1mg/L, SS<1mg/L.
Second step, pole-reversing electroosmosis
Adopt pole-reversing electroosmosis that pretreated extracting vanadium from stone coal brine waste is carried out desalting treatment; Per 2~2.5 hours reverses once in the desalting treatment process; Extracting vanadium from stone coal brine waste salinity after pole-reversing electroosmosis is handled is concentrated into 100000~110000mg/L; Obtain fresh water and dense water, wherein fresh water is back to process for extracting vanadium from stone coal.
The 3rd step, pressure reducing film distillation
The dense water that adopts pressure reducing film distillation technology that second step was obtained carries out concentration, and per-meate side vacuum tightness is 90~95kPa in the concentration process, obtains saturated brine and water of condensation, and water of condensation is back to process for extracting vanadium from stone coal, and saturated brine gets into dense pond.
The 4th step, crystallization
Crystallization be with crystallisation chamber that dense pond communicates in carry out, be added with solid NaCl in the crystallisation chamber in advance; The saturated brine that gets into crystallisation chamber from dense pond is in the crystallisation chamber crystallization, and the crystal salt after the crystallization makes Industrial Salt through evaporating brine, and the gained Industrial Salt returns process for extracting vanadium from stone coal; Crystal solution is returned dense pond through filtration, the dense hydration that the supernatant in dense pond and electrodialysis are produced also, the supernatant after the merging and dense water return the 3rd pressure reducing film distillation technology that goes on foot after heating.
The thermal source of the said heating of present embodiment is an industrial waste heat, and heated temperatures is 55~65 ℃.
Used membrane distillation assembly adopts tubular fibre formula membrane module in the described pressure reducing film distillation of present embodiment, and the filling ratio of tubular fibre formula membrane module is 30%~40%, and length-to-diameter ratio is (3~4): 1; The material of tubular fibre formula membrane module is the hydrophobicity pvdf, and mean pore size is 0.2 μ m.
Embodiment 2
A kind of integrated conduct method of extracting vanadium from stone coal brine waste.The concrete steps of its treatment process are as shown in Figure 1
The first step, pre-treatment
With embodiment 1 the first step.
Second step, pole-reversing electroosmosis
Adopt pole-reversing electroosmosis that pretreated extracting vanadium from stone coal brine waste is carried out desalting treatment; Per 2~2.5 hours reverses once in the desalting treatment process; Extracting vanadium from stone coal brine waste salinity after pole-reversing electroosmosis is handled is concentrated into 110000~120000mg/L; Obtain fresh water and dense water, wherein fresh water is back to process for extracting vanadium from stone coal.
The 3rd step, pressure reducing film distillation
With the 3rd step of embodiment 1.
The 4th step, crystallization
Except that heated temperatures is 65~75 ℃, all the other are with the 4th step of embodiment 1.
Used membrane distillation assembly adopts tubular fibre formula membrane module in the described pressure reducing film distillation of present embodiment, and the filling ratio of tubular fibre formula membrane module is 40%~60%, and length-to-diameter ratio is (4~6): 1; The material of tubular fibre formula membrane module is the hydrophobicity tetrafluoroethylene, and mean pore size is 0.2 μ m.
The heating thermal source of this embodiment is an industrial waste heat, and only needs the extracting vanadium from stone coal brine waste is heated to 55~75 ℃, when the preparation Industrial Salt, adopts the technology of evaporating brine, so energy expenditure is less; In treating processes, can all reclaim fresh water and salt wherein, the final product direct reuse has been realized the comprehensive utilization of waste water in process for extracting vanadium from stone coal, and to the environment non-secondary pollution, processing cost is low.
This embodiment also has the technology flexible characteristic, both can be used for the comprehensive treating process of extracting vanadium from stone coal brine waste, also can be used for other industry and goes up the processing of brine waste, brackish water desalination processing and sea water desaltination processing.

Claims (4)

1. the integrated conduct method of an extracting vanadium from stone coal brine waste is characterized in that the step of said integrated conduct method is:
The first step, pre-treatment
Adopt lime neutralization-soda ash to remove hard-flocculent precipitation, with the pre-treatment of extracting vanadium from stone coal brine waste extremely: Fe 2+<0.3mg/L, Mn 2+<0.1mg/L, SS<1mg/L;
Second step, pole-reversing electroosmosis
Adopt pole-reversing electroosmosis that pretreated extracting vanadium from stone coal brine waste is carried out desalting treatment; Per 2~2.5 hours reverses once in the desalting treatment process; Extracting vanadium from stone coal brine waste salinity after pole-reversing electroosmosis is handled is concentrated into 100000~120000mg/L; Obtain fresh water and dense water, wherein fresh water is back to process for extracting vanadium from stone coal;
The 3rd step, pressure reducing film distillation
The dense water that adopts pressure reducing film distillation technology that second step was obtained carries out concentration, and per-meate side vacuum tightness is 90~95kPa in the concentration process, obtains saturated brine and water of condensation, and water of condensation is back to process for extracting vanadium from stone coal, and saturated brine gets into dense pond;
The 4th step, crystallization
Crystallization be with crystallisation chamber that dense pond communicates in carry out, be added with solid NaCl in the crystallisation chamber in advance; The saturated brine that gets into crystallisation chamber from dense pond is in the crystallisation chamber crystallization, and the crystal salt after the crystallization makes Industrial Salt through evaporating brine, and the gained Industrial Salt returns process for extracting vanadium from stone coal; Crystal solution after the crystallization is returned dense pond through filtration, the dense hydration that the supernatant in dense pond and electrodialysis are produced also, the supernatant after the merging and dense water return the 3rd pressure reducing film distillation technology that goes on foot after heating.
2. the integrated conduct method of extracting vanadium from stone coal brine waste according to claim 1, the total salinity that it is characterized in that said extracting vanadium from stone coal brine waste is 10000~35000mg/L.
3. the integrated conduct method of extracting vanadium from stone coal brine waste according to claim 1, the thermal source that it is characterized in that said heating is an industrial waste heat, heated temperatures is 55~75 ℃.
4. the integrated conduct method of extracting vanadium from stone coal brine waste according to claim 1; It is characterized in that membrane distillation assembly used in the described pressure reducing film distillation adopts tubular fibre formula membrane module; The filling ratio of tubular fibre formula membrane module is 30%~60%, and length-to-diameter ratio is (3~6): 1; The material of tubular fibre formula membrane module is the hydrophobicity pvdf or is the hydrophobicity tetrafluoroethylene that mean pore size is 0.2 μ m.
CN201210110313.3A 2012-04-16 2012-04-16 Comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal Active CN102642963B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210110313.3A CN102642963B (en) 2012-04-16 2012-04-16 Comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210110313.3A CN102642963B (en) 2012-04-16 2012-04-16 Comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal

Publications (2)

Publication Number Publication Date
CN102642963A true CN102642963A (en) 2012-08-22
CN102642963B CN102642963B (en) 2014-01-01

Family

ID=46656087

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210110313.3A Active CN102642963B (en) 2012-04-16 2012-04-16 Comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal

Country Status (1)

Country Link
CN (1) CN102642963B (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103336897A (en) * 2013-06-21 2013-10-02 武汉理工大学 Environment evaluation method of stone coal vanadium-extracting solid waste
CN103601327A (en) * 2013-09-30 2014-02-26 宁夏宝塔石化科技实业发展有限公司 Near-zero-emission treating method and device for salt-containing waste water of refinery enterprise
CN104230076A (en) * 2013-06-13 2014-12-24 中国石油化工股份有限公司 Processing method of reverse osmosis concentrate during urban sewage reuse process
CN104370394A (en) * 2013-08-15 2015-02-25 北京紫光益天环境工程技术有限公司 Surface water desalting apparatus by-producing saline waste water treatment method
CN104671569A (en) * 2013-12-02 2015-06-03 财团法人工业技术研究院 Wastewater treatment system and wastewater treatment method
CN107010701A (en) * 2017-04-26 2017-08-04 武汉理工大学 Utilize the method for capacitive deionization technology separation and concentration pentavalent vanadium
CN108609775A (en) * 2018-05-25 2018-10-02 北京林业大学 A kind of method of efficient process waste incineration leachate reverse osmosis concentrated water
CN115020757A (en) * 2022-06-09 2022-09-06 四川星明能源环保科技有限公司 Electrodialysis-based method for removing organic matters in strong acid vanadium solution

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201249104Y (en) * 2008-07-21 2009-06-03 天津海之凰科技有限公司 Energy-saving type vacuum membrane distillation component device
US20100155329A1 (en) * 2008-12-18 2010-06-24 Quantumsphere, Inc. Systems and methods for forward osmosis fluid purification
CN101759313A (en) * 2009-12-08 2010-06-30 武汉科技大学 Method for recycling high-salinity heavy metal-enriched waste water from vanadium extraction from stone coal
CN101993165A (en) * 2009-08-27 2011-03-30 中国石油化工股份有限公司 Method for treating nitrochlorobenzene high-salt organic wastewater
CN102030441A (en) * 2009-09-29 2011-04-27 天津膜科力科技有限公司 Method for treating wastewater in production of sebacic acid
CN102351352A (en) * 2011-07-04 2012-02-15 昆明理工大学 Electrodialysis-efficient evaporation method for treating mining and metallurgy waste water membrane filtrating concentrate

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201249104Y (en) * 2008-07-21 2009-06-03 天津海之凰科技有限公司 Energy-saving type vacuum membrane distillation component device
US20100155329A1 (en) * 2008-12-18 2010-06-24 Quantumsphere, Inc. Systems and methods for forward osmosis fluid purification
CN101993165A (en) * 2009-08-27 2011-03-30 中国石油化工股份有限公司 Method for treating nitrochlorobenzene high-salt organic wastewater
CN102030441A (en) * 2009-09-29 2011-04-27 天津膜科力科技有限公司 Method for treating wastewater in production of sebacic acid
CN101759313A (en) * 2009-12-08 2010-06-30 武汉科技大学 Method for recycling high-salinity heavy metal-enriched waste water from vanadium extraction from stone coal
CN102351352A (en) * 2011-07-04 2012-02-15 昆明理工大学 Electrodialysis-efficient evaporation method for treating mining and metallurgy waste water membrane filtrating concentrate

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
包申旭等: "循环式电渗析器在高盐水体脱盐中的特性研究", 《武汉理工大学学报》 *

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104230076A (en) * 2013-06-13 2014-12-24 中国石油化工股份有限公司 Processing method of reverse osmosis concentrate during urban sewage reuse process
CN104230076B (en) * 2013-06-13 2015-09-16 中国石油化工股份有限公司 The treatment process of reverse osmosis concentrated water in a kind of urban sewage recycling process
CN103336897A (en) * 2013-06-21 2013-10-02 武汉理工大学 Environment evaluation method of stone coal vanadium-extracting solid waste
CN104370394A (en) * 2013-08-15 2015-02-25 北京紫光益天环境工程技术有限公司 Surface water desalting apparatus by-producing saline waste water treatment method
CN103601327A (en) * 2013-09-30 2014-02-26 宁夏宝塔石化科技实业发展有限公司 Near-zero-emission treating method and device for salt-containing waste water of refinery enterprise
CN103601327B (en) * 2013-09-30 2015-09-30 宁夏宝塔石化科技实业发展有限公司 A kind of Petrochemical Enterprises brine waste near zero release treatment process and device
CN104671569A (en) * 2013-12-02 2015-06-03 财团法人工业技术研究院 Wastewater treatment system and wastewater treatment method
CN107010701A (en) * 2017-04-26 2017-08-04 武汉理工大学 Utilize the method for capacitive deionization technology separation and concentration pentavalent vanadium
CN108609775A (en) * 2018-05-25 2018-10-02 北京林业大学 A kind of method of efficient process waste incineration leachate reverse osmosis concentrated water
CN115020757A (en) * 2022-06-09 2022-09-06 四川星明能源环保科技有限公司 Electrodialysis-based method for removing organic matters in strong acid vanadium solution

Also Published As

Publication number Publication date
CN102642963B (en) 2014-01-01

Similar Documents

Publication Publication Date Title
CN102642963B (en) Comprehensive treatment method of salt-contained waste water produced by extracting vanadium from stone coal
Panagopoulos Brine management (saline water & wastewater effluents): Sustainable utilization and resource recovery strategy through Minimal and Zero Liquid Discharge (MLD & ZLD) desalination systems
Sahu A comprehensive review of saline effluent disposal and treatment: conventional practices, emerging technologies, and future potential
CN107459200B (en) High-salt-content wastewater salinity resource recovery process
CN102260006B (en) Method for treating heavy-metal-containing wastewater membrane filtration concentrated liquid
CN106315991B (en) A kind of point salt technique for industrial wastewater
CN105152443A (en) Method and system for recycling crystallized salt resources in high-salt-content wastewater zero discharge
CN101481190B (en) Process for treating saponification wastewater by chlorohydrination
CN101759313B (en) Method for recycling high-salinity heavy metal-enriched waste water from vanadium extraction from stone coal
CN105084630A (en) Oil refining catalyst wastewater zero-discharging treatment method
CN101987767B (en) Method for producing wastewater with high ammonia nitrogen and high salinity by treating rare earth with membrane integration
CN102725236A (en) Method and system for reduction of scaling in purification of aqueous solutions
CN103739132A (en) High-salinity industrial wastewater reusing treatment process
CN203360035U (en) Comprehensive concentrated-seawater utilization device with solar pool
CN103771642A (en) Recycling method for saponified ammonium-sulfate wastewater in rare soil
CN104085933A (en) High-salinity and high organic matter wastewater treatment process
CN101928088A (en) Method for treating reverse osmosis concentrated water of petrochemical enterprises
CN104230124B (en) Coal chemical industry wastewater zero emission technique and specific equipment thereof
CN102030441A (en) Method for treating wastewater in production of sebacic acid
CN105293805A (en) High-salinity high-hardness waste water zero-discharge processing apparatus and method thereof
US20220017385A1 (en) Temperature swing solvent extraction for descaling of feedstreams
CN105198141A (en) High-temperature high-salinity wastewater zero-discharging method
CN105236650A (en) Wastewater processing method
CN102311193B (en) Method for treating filter cake filter-press filtrate in polyolefin catalyst production
US20230242418A1 (en) Temperature swing solvent extraction for descaling of feedstreams

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant