CN212770291U - Seawater comprehensive utilization system - Google Patents

Seawater comprehensive utilization system Download PDF

Info

Publication number
CN212770291U
CN212770291U CN202021463374.4U CN202021463374U CN212770291U CN 212770291 U CN212770291 U CN 212770291U CN 202021463374 U CN202021463374 U CN 202021463374U CN 212770291 U CN212770291 U CN 212770291U
Authority
CN
China
Prior art keywords
seawater
comprehensive utilization
heat exchanger
fresh water
pipeline
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.)
Active
Application number
CN202021463374.4U
Other languages
Chinese (zh)
Inventor
田江南
张恬
吴宇晨
李红军
徐淑姣
周军
刘军梅
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.)
North China Power Engineering Co Ltd of China Power Engineering Consulting Group
North China Power Engineering Beijing Co Ltd
Original Assignee
North China Power Engineering Co Ltd of China Power Engineering Consulting Group
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 North China Power Engineering Co Ltd of China Power Engineering Consulting Group filed Critical North China Power Engineering Co Ltd of China Power Engineering Consulting Group
Priority to CN202021463374.4U priority Critical patent/CN212770291U/en
Application granted granted Critical
Publication of CN212770291U publication Critical patent/CN212770291U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Abstract

The utility model relates to a seawater comprehensive utilization system, which comprises a pretreatment device, a deep pretreatment device, a heat exchanger, a RO device and a fresh water tank which are sequentially connected with seawater; wherein, the RO device is additionally provided with a pipeline connected with an electrolytic bath which is additionally connected with an evaporation system; steam obtained by evaporation of the evaporation system is returned to the heat exchanger through a pipeline to exchange heat with seawater, and the heat exchanger is additionally provided with a pipeline to send fresh water obtained by steam condensation to the fresh water tank; the utility model has a utilization rate of the seawater up to 100% and no concentrated water is discharged; the heat of the steam generated by the evaporation system can be fully utilized, and the energy is saved; meanwhile, the seawater is electrolyzed into chlorine and hydrogen in the electrolytic cell, so that the comprehensive utilization rate of the seawater is further realized, and the multi-way utilization of the seawater desalination system is realized.

Description

Seawater comprehensive utilization system
Technical Field
The utility model belongs to the water treatment field, concretely relates to sea water desalination field especially indicates a sea water comprehensive utilization system.
Background
The seawater desalination technology originates from the middle of the last century, and through the development of years, the technology is mature at present and the industrialization and scale production are realized. Generally speaking, the seawater desalination technology can be roughly divided into 3 steps: (1) pretreatment of seawater, (2) advanced pretreatment, (3) seawater desalination.
At present, the seawater desalination technology mostly adopts a reverse osmosis membrane separation technology, and the technology has the advantages of simple process, convenient operation, easy control, low operation cost and the like; however, the following problems to be solved have also been raised.
Firstly, the seawater desalination system is single, and the comprehensive utilization degree of seawater is low.
Secondly, the problem of discharging a large amount of concentrated seawater occurs, and the concentrated water after seawater desalination is generally directly discharged to the sea, which can cause the salinity change of local areas of seawater and harm marine organisms.
Therefore, in order to solve the existing problems, the utility model provides a new technical scheme.
SUMMERY OF THE UTILITY MODEL
Following as the utility model discloses preferred technical scheme, but do not regard as right the utility model provides a technical scheme's restriction, through following preferred technical scheme, can be better reach and realize the utility model discloses a technical purpose and beneficial effect.
The technical problem solved by the utility model is to provide a seawater comprehensive utilization system.
The technical means adopted by the utility model are as follows.
A seawater comprehensive utilization system comprises a pretreatment device, a deep pretreatment device, a heat exchanger, an RO device and a fresh water tank which are sequentially connected with seawater.
Wherein, the RO device is additionally provided with a pipeline connected with an electrolytic bath which is additionally connected with an evaporation system; steam obtained by evaporation of the evaporation system is returned to the heat exchanger through a pipeline to exchange heat with seawater, and fresh water obtained by steam condensation is sent to the fresh water tank through another pipeline arranged on the heat exchanger.
Preferably, the RO devices comprise a primary RO device and a secondary RO device connected in series.
Preferably, the pretreatment device is a multimedia filter.
Preferably, the advanced pretreatment device is an ultrafiltration device.
Preferably, the evaporation system is a multi-effect forced circulation evaporator.
Compared with the prior art, the utility model has the following beneficial effects.
(1) The utility model discloses reach 100% to the utilization ratio of sea water, no dense water discharges to the sea.
(2) The heat of the steam generated by the evaporation system is fully utilized, and the energy is saved.
(3) The seawater is electrolyzed into chlorine and hydrogen in the electrolytic cell, so that the comprehensive utilization rate of the seawater is further realized, and the multi-way utilization of the seawater desalination system is realized.
Drawings
Fig. 1 is a schematic view of the flow structure of the present invention.
Detailed Description
The technical solution of the present invention is further explained by the following embodiments with reference to the accompanying drawings. It is obvious that the described embodiments are only some of the embodiments of the present invention, and not all of them. Based on the embodiments of the present invention, all other embodiments obtained by a person skilled in the art without any creative work belong to the protection scope of the present embodiment.
Referring to fig. 1, the flow structure of the present invention is schematically illustrated, and each component used herein is a conventional mature device or apparatus. As shown in the figure, a seawater comprehensive utilization system, it contains: the system comprises a pretreatment device 1, a deep pretreatment device 2, a heat exchanger 3, an RO device 4 and a fresh water tank 5 which are sequentially connected with seawater; wherein, the RO device 4 is additionally provided with a pipeline connected with an electrolytic bath 6, and the electrolytic bath 6 is additionally connected with an evaporation system 7.
Further, steam obtained by evaporation of the evaporation system 7 is returned to the heat exchanger 3 through a pipeline to exchange heat with seawater, and the heat exchanger 3 is additionally provided with a pipeline to condense the steam to obtain fresh water which is sent to the fresh water tank 5.
Furthermore, the RO device 4 further comprises a primary RO device 41 and a secondary RO device 42 connected in sequence, and the concentrated water produced by the primary RO device 41 and the secondary RO device 42 is mixed and then flows into the electrolytic cell 6 together to perform the hydrogen production process by electrolysis.
Furthermore, the pretreatment device 1 adopts a multi-media filter; the deep pretreatment device 2 mostly adopts an ultrafiltration device; the evaporation system 7 is a multi-effect forced circulation evaporator.
When the utility model is used in practice, seawater is collected in a factory and then is firstly pumped to a pretreatment device 1, the pretreatment device 1 is a multi-medium filter, and impurities such as silt, suspended matters and colloid and organisms such as algae in the seawater are removed in the multi-medium filter; then the effluent of the multi-media filter flows into an advanced pretreatment device 2, the advanced pretreatment device 2 is an ultrafiltration device, and suspended matters in the seawater are further removed under the treatment of the ultrafiltration device; the outlet water of the ultrafiltration device is subjected to heat exchange in the heat exchanger and is heated to 15-25 ℃, and the temperature is favorable for the operation of the two-stage RO device.
Therefore, the heated seawater firstly enters the primary RO device 41 for desalination, the fresh water produced by the primary RO device 41 then enters the secondary RO device 42 for treatment, and finally the fresh water produced by the secondary RO device 42 is pumped to the fresh water tank 5 through a pipeline.
Meanwhile, the concentrated water produced by the first-stage RO device 41 and the second-stage RO device 42 flows into the electrolytic tank 6 through a pipeline after being mixed, and the inlet water of the upper-stage unit is further concentrated and electrolyzed in the electrolytic tank 6, so that part of the inlet water of the upper-stage unit is electrolyzed to produce hydrogen and chlorine, the rest of the concentrated water is sent to the evaporation system 7, and the evaporation system 7 removes the salt in the concentrated water to obtain the crystallized salt. And the steam generated by the evaporation system 7 is sent back to the heat exchanger 3 through a pipeline for waste heat utilization. Specifically, the steam and the effluent of the deep pretreatment device 2 exchange heat in the heat exchanger 3 to obtain steam condensate, i.e., fresh water, the heat exchanger 3 is further provided with a pipeline, so that the fresh water produced in the heat exchanger 3 is conveniently introduced into the fresh water tank 5, and the effluent of the heat exchanger 3 is heated to 15-25 ℃ and then sent to a next unit.
In a preferred embodiment of the present invention, the salt content of the seawater is about 30000mg/L, and the seawater is passed through the pretreatment device to remove larger marine organisms and large suspended particles from the seawater, and then flows into the deep pretreatment device. The deep pretreatment device mainly removes suspended matters in seawater, so that the SDI of the effluent is less than 3. And the outlet water of the deep pretreatment device is heated to 15-25 ℃ after passing through the heat exchanger, and the temperature is favorable for the operation of two-stage RO. The utility model discloses in the rate of recovery of one-level RO device is 45%, the rate of recovery of second grade RO device is 85%. When the concentrated water in the electrolytic cell is concentrated to 100000 mg/L, the concentrated water is discharged to an evaporation system.
The utility model has a utilization rate of the seawater up to 100%, and no concentrated water is discharged to the sea; meanwhile, the heat of the steam generated by the evaporation system is fully utilized, and the energy is saved and utilized.
The applicant states that the present invention is described in detail by the above embodiments, but the present invention is not limited to the above detailed method, i.e. the present invention is not meant to be implemented by relying on the above detailed method. It should be clear to those skilled in the art that any improvement of the present invention, to the equivalent replacement of each raw material of the present invention, the addition of auxiliary components, the selection of specific modes, etc., all fall within the protection scope and disclosure scope of the present invention.

Claims (5)

1. A seawater comprehensive utilization system is characterized by comprising a pretreatment device (1), a deep pretreatment device (2), a heat exchanger (3), an RO device (4) and a fresh water tank (5) which are sequentially connected with seawater;
wherein the RO device (4) is additionally provided with a pipeline connected with an electrolytic bath (6), and the electrolytic bath (6) is additionally connected with an evaporation system (7);
steam obtained by evaporation of the evaporation system (7) is returned to the heat exchanger (3) through a pipeline to exchange heat with seawater, and fresh water obtained by steam condensation is sent to the fresh water tank (5) through another pipeline arranged on the heat exchanger (3).
2. The seawater comprehensive utilization system of claim 1, wherein the RO apparatus (4) comprises a primary RO apparatus (41) and a secondary RO apparatus (42) connected in series.
3. A seawater comprehensive utilization system as claimed in claim 1, wherein said pretreatment device (1) is a multi-media filter.
4. The seawater comprehensive utilization system of claim 1, wherein the deep pretreatment device (2) is an ultrafiltration device.
5. A seawater comprehensive utilization system as claimed in claim 1, wherein said evaporation system (7) is a multi-effect forced circulation evaporator.
CN202021463374.4U 2020-07-22 2020-07-22 Seawater comprehensive utilization system Active CN212770291U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202021463374.4U CN212770291U (en) 2020-07-22 2020-07-22 Seawater comprehensive utilization system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202021463374.4U CN212770291U (en) 2020-07-22 2020-07-22 Seawater comprehensive utilization system

Publications (1)

Publication Number Publication Date
CN212770291U true CN212770291U (en) 2021-03-23

Family

ID=75027419

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202021463374.4U Active CN212770291U (en) 2020-07-22 2020-07-22 Seawater comprehensive utilization system

Country Status (1)

Country Link
CN (1) CN212770291U (en)

Similar Documents

Publication Publication Date Title
CN202912799U (en) Comprehensive recycling system of metal plating wastewater resources
CN107585968B (en) A kind of chlor-alkali brine waste processing system and method
WO2022143014A1 (en) Resourceful treatment system and method for sodium nitrate wastewater
CN101462804A (en) Electromembrane seawater desalination method and complete set of equipment
CN107311381A (en) A kind of reverse osmosis concentrated seawater comprehensive utilizing method and system
CN104030483A (en) Treatment method for recycling power plant circulating water sewage
CN112723640A (en) System and method for clean energy sea water desalination coupling salt difference energy power generation device
CN105399249B (en) A kind of device and method of municipal wastewater advanced treating
CN104445761A (en) Energy-saving seawater purification equipment
CN202881038U (en) Electroplating waste water separation and recycling treatment apparatus
CN212770291U (en) Seawater comprehensive utilization system
CN201901618U (en) Nickel plating wastewater treatment and recycle device
CN115676973B (en) High-concentration complex wastewater treatment and resource recovery system and working method thereof
CN116903181A (en) Treatment system for recycling washing water of power battery
CN101781041A (en) Method for desalting bitter by electromembrane method and equipment thereof
CN203807297U (en) Sewage treatment and sea water desalting device
CN115974327A (en) Nickel recovery system and process for nickel plating wastewater
CN216106468U (en) Electroplating effluent zero release processing system
CN102219341A (en) MBR (Meane Biological Reactor)-RO (Reverse Osmosis) technology-based method and device for on-line recycling electroplating wastewater
CN201722222U (en) Electroplating industry waste water treatment device by integrated film separation method
CN214360665U (en) Seawater desalination treatment system
CN114870633A (en) Process for enriching lithium in salt lake brine
CN211570183U (en) Landfill leachate treatment device
CN113698031A (en) Method and equipment for recovering precious metals from comprehensive wastewater
CN203754515U (en) Double membrane system for treating circulating water for coke dry quenching power generation

Legal Events

Date Code Title Description
GR01 Patent grant
GR01 Patent grant