CN106145416A - A kind of seawater comprehensive utilizing method - Google Patents
A kind of seawater comprehensive utilizing method Download PDFInfo
- Publication number
- CN106145416A CN106145416A CN201610662595.6A CN201610662595A CN106145416A CN 106145416 A CN106145416 A CN 106145416A CN 201610662595 A CN201610662595 A CN 201610662595A CN 106145416 A CN106145416 A CN 106145416A
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- China
- Prior art keywords
- sea water
- seawater
- utilizing method
- environment
- comprehensive utilizing
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- 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.)
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Classifications
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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
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/06—Flash evaporation
-
- 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
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- 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
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/444—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/08—Seawater, e.g. for desalination
Abstract
The invention discloses a kind of seawater comprehensive utilizing method, said method comprising the steps of: (1) filters: pumping enters sea water and sequentially passes through activated carbon filtration, microfiltration, ultrafiltration, and much filtrate is stand-by;(2) desalination: the sea water after using Membrane seawater desalination device or full-boiled process sea water desalinating unit to filter is desalinated;(3) configuration sea water culture environment: the strong brine that sea water stays after desalting plant extracts, introduces tank, and by adding nutritional labeling, human configuration becomes to be suitable for the environment of animals and plants existence.Employing the method can be effectively by whole recycle and reuse of stage products therefrom each after Seawater Treatment, it is achieved that Seawater Treatment achieves zero-emission, decreases pollution, meanwhile, creates good economic worth.
Description
Technical field
The present invention relates to seawater utilization field, particularly relate to a kind of seawater comprehensive utilizing method.
Background technology
Being stored in total moisture storage capacity about 1386 × 10 billion cubic meter of the earth, wherein ocean water is 1338 × 10 billion cubic meters,
Accounting for the 96.5% of whole world total Water, freshwater resources only account for the 3.5% of whole world total Water.And fresh water is mainly with glacier and deep
Presented in layer subsoil water, the 0.3% of what the mankind such as rivers and lakes can directly utilize the total fresh water in the fresh water Jin Zhan world.Institute
It is the matter of utmost importance that city, the whole world faces with hydropenia, has accounted for 80 countries and regions about 15 of world population sum 40%
Hundred million population fresh water are not enough, wherein 26 country about 300,000,000 people's extreme dehydration.More frighteningly, it is contemplated that by 2025, in the world will
3,000,000,000 people are had to face hydropenia, 40 countries and regions fresh water wretched insufficiencies.
Along with modern scientific and technological progress, people begin to take on the desalinization of the mode such as reverse osmosis, full-boiled process, can solve people
The demand of class fresh water in future, but traditional desalinization belongs to high energy-consuming industry, and also produced while obtaining fresh water
Strong brine discharge can cause secondary pollution, how to utilize solid matter in sea water, the effective strong brine utilizing desalination, it is achieved sea
Water desalination zero-emission is the important directions of current seawater utilization development.
Summary of the invention
It is an object of the invention to overcome the deficiencies in the prior art, it is provided that a kind of seawater comprehensive utilizing method.Use the party
Method can be effectively by whole recycle and reuse of stage products therefrom each after Seawater Treatment, it is achieved that Seawater Treatment achieves zero-emission
Putting, decrease pollution, meanwhile, each link of Seawater Treatment all can create good economic worth.
The purpose of the present invention is achieved by below scheme:
A kind of seawater comprehensive utilizing method, said method comprising the steps of:
(1) filter: pumping enters sea water and sequentially passes through activated carbon filtration, microfiltration, ultrafiltration, and much filtrate is animal wastes or algae
Material;
(2) desalination: the sea water after using Membrane seawater desalination device or full-boiled process sea water desalinating unit to filter is desalinated;
(3) configuration sea water culture environment: the strong brine that sea water stays after desalting plant extracts, introduces tank, passes through
Adding nutritional labeling, human configuration becomes to be suitable for cultivating halobiontic water environment;
Further, described animal wastes or algae substances are for Fodder making;
Further, described step (2) embrane method desalting plant is reverse osmosis membrane desalting plant;
Further, described step (2) used full-boiled process sea water desalinating unit is low temperature multiple-effect distillation device, multistage flash evaporation
Device, calm the anger distilling apparatus or solar energy desalting plant;
Further, the sea water culture environment Middle nutrition composition of described step (3) human configuration and concrete content are for for chlorine
Change sodium NaCl24~26g/L, magnesium chloride Mg Cl23~25g/L, magnesium sulfate MgSO43~4g/L, calcium chloride CaCl21~1.5g/L,
Sodium bicarbonate NaHCO30.1~0.2g/L, potassium chloride (KCl) 0.5~1g/L, sodium bromide NaBr0.05~0.06g/L, boric acid
H3BO30.05~0.06g/L, sodium silicate Na2SiO30.002~0.003g/L, sodium silicate Na2Si4O90.001~0.002g/L,
Phosphoric acid H3PO40.002g/L, chlordeneization two aluminum Al2Cl60.01~0.015g/L, ammonia NH30.002g/L, lithium nitrate
LiNO30.00010~0.00015g/L;
Further, described artificial environment is suitable for supporting ocean fishes or shrimp, artificial cultivation ocean fishes and shrimp to the requirement of water environment very
Height, volume production to be realized, it is necessary to be controlled by the various nutritional labelings of water environment, the mentioned component content in strong brine is relatively
Height, will be allocated by introducing sea water and related nutritional material, thus the yield realizing artificial cultivation ocean fishes and shrimp is increased,
The most both avoid the discharge of strong brine, it is achieved that the zero-emission after Seawater Treatment, effectively make use of the nothing in strong brine
Machine acid or salt, achieve again the purpose of artificial cultivation marine product, it is possible to the environment of conservative control artificial cultivation, thus controls to produce
Amount.
One seawater comprehensive utilizing method of the present invention, has a following beneficial effect:
The seawater comprehensive utilizing method of the present invention, effectively can all reclaim stage products therefrom each after Seawater Treatment and follow
Ring utilizes.The concentrated seawater produced currently for sea water desalinating unit mainly uses and in line enters to enter sea or straight after sea, dilution
Enter deep-well etc..In terms of the sea water desalinating unit of daily output desalination water 6 kiloton, every day will generate the concentrated seawater of 10.8 kilotons.Wherein
Still containing NaCl more than large quantity of moisture, and 420 tons and other salt a certain amount of.Using concentrated seawater as discharging of waste liquid, not only
Environment is caused reality or potential impact, and then changes the ecological balance of ocean, and abandoned whole salts and
Water resource, it is clear that the seawater resources of preciousness could not be made full use of, be allowed to lose after having got it.Additionally, enter deep-well sooner or later
Land can be polluted;Rush dilute heel row sea and more waste freshwater resources.The seawater comprehensive utilizing method of the present invention, first passes around filter institute
Obtaining solid matter and can prepare feedstuff, the sea water of desalination can directly be drunk, and the strong brine after desalination can be formulated as people
The water environment of work cultivation seafood, it may be said that achieve Seawater Treatment and achieve zero-emission, decrease pollution, create very meanwhile
Good economic worth.
Detailed description of the invention
In order to make those skilled in the art be more fully understood that technical scheme, below in conjunction with embodiment to this
Bright technical scheme is described in further detail.
Embodiment 1
A kind of seawater comprehensive utilizing method, said method comprising the steps of:
(1) filter: pumping enters sea water and sequentially passes through activated carbon filtrations, microfiltration, ultrafiltration, much filtrate be mostly animal wastes with
Algae, nitrogen and phosphorus content is high, prepares animal feed.
(2) desalination: the sea water after using multistage flash distillation device to filter is desalinated;
(3) configuration sea water culture environment: the strong brine that sea water stays after multistage flash evaporation desalting plant extracts, introduces water storage
Pond, by adding nutritional labeling, human configuration becomes to be suitable for the environment of ocean fishes existence, the water environment of the artificial cultivation ocean fishes configured
Nutritional labeling and content particularly as follows: sodium chloride nacl 24.20g/L, magnesium chloride Mg Cl23.80g/L, magnesium sulfate
MgSO43.60g/L, calcium chloride CaCl21.20g/L, sodium bicarbonate NaHCO30.15g/L, potassium chloride (KCl) 0.62g/L, sodium bromide
NaBr0.056g/L, boric acid H3BO30.055g/L, sodium silicate Na2SiO30.0025g/L, sodium silicate Na2Si4O90.0014g/L、
Phosphoric acid H3PO40.002g/L, chlordeneization two aluminum Al2Cl60.013g/L, ammonia NH30.002g/L, lithium nitrate LiNO30.00012g/L。
Embodiment 2
A kind of seawater comprehensive utilizing method, said method comprising the steps of:
(1) filter: pumping enters sea water and sequentially passes through activated carbon filtration, microfiltration, ultrafiltration, and much filtrate prepares feedstuff.
(2) desalination: the sea water after using low-temperature multi-effect vaporising device to filter is desalinated;
(3) configuration sea water culture environment: the strong brine that sea water stays after desalting plant extracts, introduces tank, passes through
Adding nutritional labeling, human configuration becomes to be suitable for the environment of shrimp existence, and nutritional labeling and content in environment are concrete: sodium chloride
NaCl25.51g/L, magnesium chloride Mg Cl24.42g/L, magnesium sulfate MgSO43.66g/L, calcium chloride CaCl21.45g/L, sodium bicarbonate
NaHCO30.18g/L, potassium chloride (KCl) 0.62g/L, sodium bromide NaBr0.052g/L, boric acid H3BO30.058g/L, sodium silicate
Na2SiO30.0018g/L, sodium silicate Na2Si4O90.0016g/L, phosphoric acid H3PO40.002g/L, chlordeneization two aluminum
Al2Cl60.013g/L, ammonia NH30.002g/L, lithium nitrate LiNO30.00013g/L。
Embodiment 3
A kind of seawater comprehensive utilizing method, said method comprising the steps of:
(1) filter: pumping enters sea water and sequentially passes through activated carbon filtrations, microfiltration, ultrafiltration, much filtrate be mostly animal wastes with
Algae, nitrogen and phosphorus content is high, prepares animal feed.
(2) desalination: the sea water after using reverse osmosis membrane apparatus to filter is desalinated;
(3) configuration sea water culture environment: the strong brine that sea water stays after reverse osmosis membrane desalting plant extracts, introduces water storage
Pond, by adding nutritional labeling, human configuration becomes to be suitable for the environment of bathypelagic fish existence, nutritional labeling in environment and containing measurer
Body, the water environment of the artificial cultivation bathypelagic fish configured is: sodium chloride nacl 24.90g/L, magnesium chloride Mg Cl24.00g/L, sulfur
Acid magnesium MgSO43.80g/L, calcium chloride CaCl21.32g/L, sodium bicarbonate NaHCO30.16g/L, potassium chloride (KCl) 0.76g/L, bromine
Change sodium NaBr0.058g/L, boric acid H3BO30.057g/L, sodium silicate Na2SiO30.002g/L, sodium silicate Na2Si4O90.0014g/
L, phosphoric acid H3PO40.002g/L, chlordeneization two aluminum Al2Cl60.014g/L, ammonia NH30.002g/L, lithium nitrate LiNO30.00011g/
L。
The seawater comprehensive utilizing method of the present invention, first passes around filter gained solid matter and can prepare feedstuff, the sea of desalination
Water can directly be drunk, and the strong brine after desalination can the formulated water environment as artificial cultivation seafood, it may be said that achieve
Seawater Treatment achieves zero-emission, decreases pollution, meanwhile, creates good economic worth.
The above, only presently preferred embodiments of the present invention, not the present invention is made any pro forma restriction;All
The those of ordinary skill of the industry all can shown in by specification and the above and implement the present invention swimmingly;But, all familiar
Professional and technical personnel, in the range of without departing from technical solution of the present invention, may utilize disclosed above technology contents and makes
A little change, the equivalent variations modifying and develop, be the Equivalent embodiments of the present invention;Meanwhile, all realities according to the present invention
The change of any equivalent variations that above example is made by matter technology, modify and differentiation etc., all still fall within the technology of the present invention
Within the protection domain of scheme.
Claims (6)
1. a seawater comprehensive utilizing method, it is characterised in that comprise the following steps:
(1) filter: pumping enters sea water and sequentially passes through activated carbon filtration, microfiltration, ultrafiltration, and much filtrate is animal wastes or algae thing
Matter;
(2) desalination: the sea water after using Membrane seawater desalination device or full-boiled process sea water desalinating unit to filter is desalinated;
(3) configuration sea water culture environment: the strong brine that sea water stays after desalting plant extracts, introduces tank, by adding
Nutritional labeling, human configuration becomes to be suitable for cultivating halobiontic water environment.
Seawater comprehensive utilizing method the most according to claim 1, it is characterised in that: described animal wastes or algae substances
For Fodder making.
Seawater comprehensive utilizing method the most according to claim 1, it is characterised in that: described step (2) embrane method desalting plant
For reverse osmosis membrane desalting plant.
Seawater comprehensive utilizing method the most according to claim 1, it is characterised in that: described step (2) used full-boiled process sea
Water desalination apparatus is low temperature multiple-effect distillation device, multistage flash distillation device, calm the anger distilling apparatus or solar energy desalting plant.
Seawater comprehensive utilizing method the most according to claim 1, it is characterised in that: the sea of described step (3) human configuration
Water breeding environment Middle nutrition composition and concrete content is: sodium chloride nacl 24~26g/L, magnesium chloride Mg Cl23~25g/L, sulphuric acid
Magnesium MgSO43~4g/L, calcium chloride CaCl21~1.5g/L, sodium bicarbonate NaHCO30.1~0.2g/L, potassium chloride (KCl) 0.5~
1g/L, sodium bromide NaBr0.05~0.06g/L, boric acid H3BO30.05~0.06g/L, sodium silicate Na2SiO30.002~
0.003g/L, sodium silicate Na2Si4O90.001~0.002g/L, phosphoric acid H3PO40.002g/L, chlordeneization two aluminum Al2Cl60.01~
0.015g/L, ammonia NH30.002g/L, lithium nitrate LiNO30.00010~0.00015g/L.
Seawater comprehensive utilizing method the most according to claim 5, it is characterised in that: described artificial seawater breeding environment is suitable for
Support ocean fishes or shrimp.
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107155972A (en) * | 2017-06-21 | 2017-09-15 | 厦门中研融源科技有限公司 | A kind of fresh water seawater method for transformation and cyclic utilization system |
CN110904914A (en) * | 2018-01-29 | 2020-03-24 | 陈凯 | Water transfer method for sea water from east to west to south |
CN114835198A (en) * | 2022-06-09 | 2022-08-02 | 广东海水工程科技有限公司 | Process for breeding artemia by utilizing seawater to desalt strong brine |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101967026A (en) * | 2010-09-03 | 2011-02-09 | 葛文宇 | Energy-saving emission-reduction seawater comprehensive utilizing method |
CN103602589A (en) * | 2013-11-06 | 2014-02-26 | 陈亚民 | Method for utilizing concentrated seawater generated by seawater desalinization device |
CN105174545A (en) * | 2015-09-23 | 2015-12-23 | 江苏省科建成套设备有限公司 | Multi-membrane-method sea water desalination integrated device |
CN205295039U (en) * | 2015-12-09 | 2016-06-08 | 中国海洋大学 | Electrically -driven membrane seawater desalination integrated equipment |
-
2016
- 2016-08-12 CN CN201610662595.6A patent/CN106145416A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101967026A (en) * | 2010-09-03 | 2011-02-09 | 葛文宇 | Energy-saving emission-reduction seawater comprehensive utilizing method |
CN103602589A (en) * | 2013-11-06 | 2014-02-26 | 陈亚民 | Method for utilizing concentrated seawater generated by seawater desalinization device |
CN105174545A (en) * | 2015-09-23 | 2015-12-23 | 江苏省科建成套设备有限公司 | Multi-membrane-method sea water desalination integrated device |
CN205295039U (en) * | 2015-12-09 | 2016-06-08 | 中国海洋大学 | Electrically -driven membrane seawater desalination integrated equipment |
Non-Patent Citations (1)
Title |
---|
王朝瑾等编著: "《水产生物流通与加工贮藏技术》", 30 November 2007, 上海:上海科学技术出版社 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107155972A (en) * | 2017-06-21 | 2017-09-15 | 厦门中研融源科技有限公司 | A kind of fresh water seawater method for transformation and cyclic utilization system |
CN110904914A (en) * | 2018-01-29 | 2020-03-24 | 陈凯 | Water transfer method for sea water from east to west to south |
CN114835198A (en) * | 2022-06-09 | 2022-08-02 | 广东海水工程科技有限公司 | Process for breeding artemia by utilizing seawater to desalt strong brine |
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