CN102745870A - Factory aquaculture water circulating device - Google Patents
Factory aquaculture water circulating device Download PDFInfo
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- CN102745870A CN102745870A CN201210259070XA CN201210259070A CN102745870A CN 102745870 A CN102745870 A CN 102745870A CN 201210259070X A CN201210259070X A CN 201210259070XA CN 201210259070 A CN201210259070 A CN 201210259070A CN 102745870 A CN102745870 A CN 102745870A
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Abstract
The invention discloses a factory aquaculture water circulating device. Aquaculture wastewater is subjected to solid-liquid separation treatment to remove most of solid particles, remaining soluble organic matters, ammonia nitrogen and nitrite nitrogen are primarily biologically treated, the soluble organic matters, the ammonia nitrogen and the nitrite nitrogen remaining in the aquaculture wastewater are subjected to ozone contact oxidation, and the aquaculture wastewater subjected to the ozone contact oxidation treatment is aerated to reduce or remove strong oxides which are produced by the ozone contact oxidation treatment and dissolved in the aquaculture water. The device has the advantages of novel structure, complete oxidizing substance degradation, low use cost, high safety, low environmental pressure and quick effect.
Description
Technical field
The present invention relates to the refining plant of intensive culture water body, relate in particular to the industrialized culture water circle device.
Background technology
Recirculated water industrialized aquiculture system core concept is based on brine disposal and system's control techniques, builds pure and stable water body environment, simulate all kinds of marine products interdependent natural ocean environment, make it breed growth according to the mode of letting nature take its course most.As; Like Chinese invention patent " a kind of industrial fish farming ecological waste water cycle of treatment is utilized system "; The patent No. 200810008753.1, this system comprises: circulating water treatment facility, equipment such as fishpond, ultralow lift propeller pump, jet aeration oxygenation facility, foam separation facility, supplied with pure oxygen device, temperature control facility, artificial swamp; Adopt open big flow supply canal, backwater canal to replace closed conduit.Adopt the foam separation facility to substitute Protein Skimmer; Adopt deep-well temperature control facility to substitute intensification, cooling system; Adopt jet aeration oxygenation facility to substitute oxygenating machine, gas stone and tracheae, adopt artificial swamp waterplant and economic filtrate to substitute purification filtering equipment such as solid-liquid separation.Yet prior art adopts modes such as microbially decontaminate, natural aeration more, and speed is slow, receive such environmental effects such as temperature, illumination, and poor to the extreme condition tolerance, and comparatively expend the space, volume is big, thereby limiting factor is more, unfavorable popularization.
Summary of the invention
The objective of the invention is to prior art provide the degraded of a kind of novel structure, oxidizing substance thoroughly, to aquaculture organism poison low, use cost is cheap, security good, environmental stress is little, industrialized culture water circle device fast takes effect.
The present invention solves the problems of the technologies described above the technical scheme that is adopted: the industrialized culture water circle device comprises having the into breed pond of water and water-freeing arrangement, wherein: culture the pond water-freeing arrangement and be connected with biochemistry pool through solid-liquid separator; Biochemistry pool also is connected with the diversion three-way valve; A path direct pipe connection backflow T-valve of diversion three-way valve also is back to the breed pond; Another path of diversion three-way valve then connects the backflow T-valve except that the ozone water treatment system of residual ozone in anhydrating and strong oxide compound as required through carrying out the supersaturation ozonization to breed water.
Be to optimize technique scheme, the measure of taking also comprises: ozone water treatment system has the ozone solution that ozone and water are fully contacted be water that is connected with the diversion three-way valve and reaches oversaturated oxidizing tower; Oxidizing tower also pipe connection has the reduction tower; The reduction tower is through being equipped with the pipe connection backflow T-valve of detector.
Oxidizing tower is connected with ozonizer; The reduction tower is connected with pneumatic pump; Detector is connected with power controller; Ozonizer connects power controller.
The ozone reduction tower comprises the tank body of hollow cavity, and wherein: the middle part of tank inner chamber is provided with protruded packing; Be provided with spray header near the top of tank inner chamber; The bottom of tank inner chamber is provided with the micropore air-spreading disk; Near the tank base side is run through and is provided with water outlet.External water source sprays into tank interior through spray header, and the micropore air-spreading disk that is positioned at tank base connects external air source.Source of the gas is air or reducing gas.The water of gas and the external water source of ejection is sentenced big surface in contact at protruded packing and is amassed mode and mix, and neutralizes and removes the material with oxidisability in the external water source water.Water after the processing is discharged from water outlet.
Tank base has blow-off pipe; The tank body top also has exhaust port.Exhaust port is discharged unnecessary gas, and balance tank body pressure inside, and the acquisition environment of stable liquid level sensor reduces and disturbs.
Tank body has riser near the top.Riser is a security measures, when malfunctioning situation appears in system, is the danger that prevents that too high water level from causing, thereby the design riser is discharged unnecessary water.
Tank base is attached with liquid level sensor; The liquid level sensor of bottom can be according to the flow velocity of the intravital liquid level change control of jar external water source to the spray header water filling; The bottom also has supporting leg.Strong oxide compound is ozone or bromic acid or its combination.
Because industrialized culture water circle device of the present invention; Adopted breeding wastewater at first after most of solid particulate is removed in the solid-liquid separation processing; Behind the remaining dissolved organic matter of biological mode rough handling, ammonia nitrogen, nitrous acid nitrogen, remain in dissolved organic matter, ammonia nitrogen, nitrous acid nitrogen in the breeding wastewater through O3 contacted oxidation; Breeding wastewater after O3 contacted oxidation is handled is again through reducing with air aeration or removing to be dissolved in and handle methods and the technique means such as strong oxide compound that produces because of O3 contacted oxidation in the breeding wastewater.Thereby the present invention has the advantage that the oxidizing substance degraded is thorough, low to the aquaculture organism murder by poisoning, use cost is cheap, security is good.
Description of drawings
Fig. 1 is embodiment of the invention reduction tower structure synoptic diagram;
Fig. 2 connects synoptic diagram for the embodiment of the invention.
Embodiment
Below in conjunction with attaching embodiment the present invention is described in further detail.
Drawing reference numeral explanation: culture pond 1; Solid-liquid separator 2; Biochemistry pool 3; Diversion three-way valve 4; Oxidizing tower 5; Ozonizer 51; Oxygen canister 52; Reduction tower 6; Tank body 61; Blow-off pipe 61a; Supporting leg 61b; Top manhole 611; Exhaust port 612; Riser 613; Protruded packing 614; Spray header 615; Water outlet 616; Visor 617; Side manhole 618; Micropore air-spreading disk 619; Liquid level sensor 621; Liquidometer 622; Liquid meter 623; Gas meter 624; Pneumatic pump 63; Detector 7; Power controller 71; Backflow T-valve 8.
Embodiment: referring to figs. 1 through Fig. 2, the industrialized culture water circle device is applied to the industrialized culture water circle device, and this device has the into breed pond 1 of water and water-freeing arrangement, wherein: culture pond 1 water-freeing arrangement and be connected with biochemistry pool 3 through solid-liquid separator 2; Biochemistry pool 3 also is connected with diversion three-way valve 4; The direct pipe connection backflow of a path T-valve 8 of diversion three-way valve 4 also is back to breed pond 1; Another path of diversion three-way valve 4 then connects backflow T-valve 8 except that the ozone water treatment system of residual ozone in anhydrating and strong oxide compound as required through carrying out the supersaturation ozonization to breed water.
Ozone water treatment system has the ozone solution that ozone and water are fully contacted be water that is connected with diversion three-way valve 4 and reaches oversaturated oxidizing tower 5; Oxidizing tower 5 is gone back pipe connection has reduction tower 6; Reduction tower 6 is through being equipped with the pipe connection backflow T-valve 8 of detector 7.
Oxidizing tower 5 is connected with ozonizer 51; Reduction tower 6 is connected with pneumatic pump 63; Detector 7 is connected with power controller 71; Ozonizer 51 connects power controller 71.Ozone reduction tower 6 comprises the tank body 61 of hollow cavity, and wherein: the middle part of tank body 61 inner chambers is provided with protruded packing 614; Be provided with spray header 615 near the top of tank body 61 inner chambers; The bottom of tank body 61 inner chambers is provided with micropore air-spreading disk 619; Near tank body 61 bottoms side is run through and is provided with water outlet 616.External water source sprays into tank body 61 inside through spray header 615, and the micropore air-spreading disk 619 that is positioned at tank body 61 bottoms connects external air source.Source of the gas is air or reducing gas.The water of gas and the external water source of ejection is sentenced big surface in contact at protruded packing 614 and is amassed mode and mix, and neutralizes and removes the material with oxidisability in the external water source water.Water after the processing is discharged from water outlet 616.Tank body 61 bottoms have blow-off pipe 61a; Tank body 61 tops also have exhaust port 612.Exhaust port 612 is discharged unnecessary gas, and balance tank body 61 pressure inside, and the acquisition environment of stable liquid level sensor 621 reduces and disturbs.Tank body has riser 613 near 61 tops.Riser 613 is a security measures, when malfunctioning situation appears in system, is the danger that prevents that too high water level from causing, thereby design riser 613 is discharged unnecessary water.
Tank body 61 bottoms are attached with liquid level sensor 621.The liquid level sensor 621 of bottom can be according to the flow velocity of the control of the liquid level change in the tank body 61 external water source to spray header 615 water fillings.The bottom also has supporting leg 61b.
Tank body 61 sides are equipped with liquidometer 622.Liquidometer 622 supplies the personal monitoring.Micropore air-spreading disk 619 can connect external air source through gas meter 624; Spray header 615 can connect external water source through liquid meter 623.Gas meter 624, liquid meter 623, liquid level sensor 621 are regulated and control the speed of air inlet, water inlet through the coupling of detection data.Tank body 61 tops are shaped on top manhole 611; Tank body 61 sides are shaped at least one side manhole 618; Bottom, tank body 61 side is run through and is provided with visor 617.
Culture pond 1 and in breeding process, can produce a large amount of objectionable impuritiess, batch production particularly superset spend in the cultivating system, approximately for the very big after the meeting toxic action of cultured fishes.Therefore effectively remove these materials, have realistic meaning for reducing the breeding wastewater discharging.The waste water of culturing pond 1 is through removing solid waste earlier through solid-liquid separator 2, again through biochemistry pool 3 with the remaining dissolved organic matter of biological mode rough handling, ammonia nitrogen, nitrous acid nitrogen.The water of handling through biochemistry pool 3 is divided into two paths as required through diversion three-way valve 4.Wherein an elder generation is through oxidizing tower 5; Oxygen in the oxygen canister 52 forms a large amount of ozone and injects oxidizing tower 5 and mix with the abundant aeration of water after ozonizer 51 is handled; Make the ozone in the water reach hypersaturated state; With all oxidations such as dissolved organic matter, ammonia nitrogen, nitrous acid nitrogen,, and attach the effect of having played kill microorganisms with this with reduced toxicity.Yet, because a large amount of injections of ozone, but injected new toxic substance removing the toxic while of organism, in this process like ozone, bromic acid etc.Just can be reused for breed after must these materials being removed.Water after oxidizing tower 5 is handled is transported in the reduction tower 6.The bottom of tank body 61 inner chambers is provided with micropore air-spreading disk 619; Near tank body 61 bottoms side is run through and is provided with water outlet 616.External water source sprays into tank body 61 inside through spray header 615, and the micropore air-spreading disk 619 that is positioned at tank body 61 bottoms connects external air source.Source of the gas is an air.The gas of ejection is sentenced the long-pending mode of big surface in contact with water at protruded packing 614 and is mixed, and removes the material with oxidisability in anhydrating.Water after the processing is discharged into backflow T-valve 8 from water outlet 616.Detector 7 on pipeline between reduction tower 6 and the backflow T-valve 8 is with ozone in water, bromic acid content detection and feed back to power controller 71, and then the power of control ozonizer 51, and bromic acid or ozone content are higher than safety value in the water of anti-backflow.When bromic acid in the water that refluxes or ozone is too high and for a long time can not be when reducing ozonizer 51 and reduce, diversion three-way valve 4 directly is back to water through another loop and cultures pond 1 through backflow T-valve 8, poison cultured fishes to avoid materials such as bromic acid.Owing to adopt the present invention, can reduce the use of chemical water purification agent, ecological friendly, less to environmental stress.
Although combined preferred embodiment the present invention has been described; Right its is not in order to limit the present invention; Any those skilled in the art; Under the situation that does not break away from the spirit and scope of the present invention, can implement the displacement and the modification of various changes, coordinator to the theme of listing here, so protection scope of the present invention is as the criterion when looking the scope thereof that is proposed.
Claims (6)
1. industrialized culture water circle device comprises having the into breed pond (1) of water and water-freeing arrangement, and it is characterized in that: described breed pond (1) water-freeing arrangement is connected with biochemistry pool (3) through solid-liquid separator (2); Described biochemistry pool (3) also is connected with diversion three-way valve (4); The direct pipe connection backflow of a path T-valve (8) of described diversion three-way valve (4) also is back to described breed pond (1); Another path of described diversion three-way valve (4) then connects described backflow T-valve (8) except that the ozone water treatment system of residual ozone in anhydrating and strong oxide compound as required through carrying out the supersaturation ozonization to breed water.
2. industrialized culture water circle device according to claim 1 is characterized in that: described ozone water treatment system has the ozone solution that ozone and water are fully contacted be water that is connected with described diversion three-way valve (4) and reaches oversaturated oxidizing tower (5); Described oxidizing tower (5) is gone back pipe connection has reduction tower (6); Described reduction tower (6) is through the described backflow T-valve of the pipe connection that detector (7) is installed (8).
3. industrialized culture water circle device according to claim 2 is characterized in that: described oxidizing tower (5) is connected with ozonizer (51); Described reduction tower (6) is connected with pneumatic pump (63); Described detector (7) is connected with power controller (71); Described ozonizer (51) connects described power controller (71).
4. industrialized culture water circle device according to claim 3 is characterized in that: ozone reduction tower (6), comprise the tank body (61) of hollow cavity, and wherein: the middle part of tank body (61) inner chamber is provided with protruded packing (614); Be provided with spray header (615) near the top of tank body (61) inner chamber; The bottom of tank body (61) inner chamber is provided with micropore air-spreading disk (619); Near tank body (61) bottom side is run through and is provided with water outlet (616).
5. industrialized culture water circle device according to claim 4 is characterized in that: the bottom of described tank body (61) has blow-off pipe (61a); Described tank body (61) top also has exhaust port (612); Described tank body (61) has riser (613) near the top.
6. industrialized culture water circle device according to claim 5 is characterized in that: described tank body (61) bottom is attached with liquid level sensor (621); The liquid level sensor of described bottom (621) can be according to the flow velocity of the control of the liquid level change in the tank body (61) external water source to spray header (615) water filling; Described bottom also has supporting leg (61b).
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Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103112996A (en) * | 2013-02-06 | 2013-05-22 | 姜汉平 | Aquaculture water circulation purification method and device |
CN103238554A (en) * | 2013-05-20 | 2013-08-14 | 天津市兴盛海淡水养殖有限责任公司 | Ecotype enclosed method for culturing fish through circulation water |
CN103253830A (en) * | 2013-05-30 | 2013-08-21 | 浙江海洋学院 | Biological pollution control method for industrial aquaculture wastewater |
CN103265108A (en) * | 2013-05-30 | 2013-08-28 | 浙江海洋学院 | Factory breeding wastewater bio-pollution removal device |
CN104521859A (en) * | 2014-12-29 | 2015-04-22 | 浙江海洋学院普陀科学技术学院 | Dual land farming tank |
CN104521861A (en) * | 2014-12-29 | 2015-04-22 | 浙江海洋学院普陀科学技术学院 | Low-ammonia-nitrogen super-intensive aquiculture system |
CN113024033A (en) * | 2021-03-15 | 2021-06-25 | 云南省设计院集团工程投资有限公司 | Process for deeply treating sewage discharge of livestock and poultry breeding industry |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH11346595A (en) * | 1998-06-03 | 1999-12-21 | Hitachi Zosen Corp | Cleaning of water for raising aquatic organism |
EP1659098A2 (en) * | 2003-06-19 | 2006-05-24 | Kansai Paint Co., Ltd. | Method for clarifying waste water containing organic material |
CN1981574A (en) * | 2005-12-15 | 2007-06-20 | 上海水产大学 | Aquiculturing system process for works with circulating water |
CN101538102A (en) * | 2009-04-27 | 2009-09-23 | 同济大学 | Ozone-bacteria filter system for advanced treatment of hardly-degradable organic wastewater |
CN101602562A (en) * | 2008-06-12 | 2009-12-16 | 中国科学院生态环境研究中心 | A kind of high-safety regenerated water deep treatment system |
CN201832630U (en) * | 2010-08-16 | 2011-05-18 | 长春黄金研究院 | Reactor for advanced treatment of waste liquid containing cyanide and cyanide derivative |
CN202729952U (en) * | 2012-07-25 | 2013-02-13 | 浙江海洋学院 | Ozone intensive aquaculture device |
-
2012
- 2012-07-25 CN CN201210259070XA patent/CN102745870A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH11346595A (en) * | 1998-06-03 | 1999-12-21 | Hitachi Zosen Corp | Cleaning of water for raising aquatic organism |
EP1659098A2 (en) * | 2003-06-19 | 2006-05-24 | Kansai Paint Co., Ltd. | Method for clarifying waste water containing organic material |
CN1981574A (en) * | 2005-12-15 | 2007-06-20 | 上海水产大学 | Aquiculturing system process for works with circulating water |
CN101602562A (en) * | 2008-06-12 | 2009-12-16 | 中国科学院生态环境研究中心 | A kind of high-safety regenerated water deep treatment system |
CN101538102A (en) * | 2009-04-27 | 2009-09-23 | 同济大学 | Ozone-bacteria filter system for advanced treatment of hardly-degradable organic wastewater |
CN201832630U (en) * | 2010-08-16 | 2011-05-18 | 长春黄金研究院 | Reactor for advanced treatment of waste liquid containing cyanide and cyanide derivative |
CN202729952U (en) * | 2012-07-25 | 2013-02-13 | 浙江海洋学院 | Ozone intensive aquaculture device |
Non-Patent Citations (2)
Title |
---|
THOMAS GROSVENOR: "自来水中臭氧副产物的生成及其控制", 《净水技术》 * |
郑波等: "臭氧处理海水生成氧化物对扁藻生长的影响", 《青岛海洋大学学报》 * |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103112996A (en) * | 2013-02-06 | 2013-05-22 | 姜汉平 | Aquaculture water circulation purification method and device |
CN103238554A (en) * | 2013-05-20 | 2013-08-14 | 天津市兴盛海淡水养殖有限责任公司 | Ecotype enclosed method for culturing fish through circulation water |
CN103238554B (en) * | 2013-05-20 | 2014-06-25 | 天津市兴盛海淡水养殖有限责任公司 | Ecotype enclosed method for culturing fish through circulation water |
CN103253830A (en) * | 2013-05-30 | 2013-08-21 | 浙江海洋学院 | Biological pollution control method for industrial aquaculture wastewater |
CN103265108A (en) * | 2013-05-30 | 2013-08-28 | 浙江海洋学院 | Factory breeding wastewater bio-pollution removal device |
CN103253830B (en) * | 2013-05-30 | 2015-09-30 | 浙江海洋学院 | Biological pollution control method for industrial aquaculture wastewater |
CN104521859A (en) * | 2014-12-29 | 2015-04-22 | 浙江海洋学院普陀科学技术学院 | Dual land farming tank |
CN104521861A (en) * | 2014-12-29 | 2015-04-22 | 浙江海洋学院普陀科学技术学院 | Low-ammonia-nitrogen super-intensive aquiculture system |
CN113024033A (en) * | 2021-03-15 | 2021-06-25 | 云南省设计院集团工程投资有限公司 | Process for deeply treating sewage discharge of livestock and poultry breeding industry |
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Application publication date: 20121024 |