CN104585121B - Ecological fish tank for driving water circulation and removing total nitrogen through aeration and method for breeding edible fish with ecological fish tank - Google Patents
Ecological fish tank for driving water circulation and removing total nitrogen through aeration and method for breeding edible fish with ecological fish tank Download PDFInfo
- Publication number
- CN104585121B CN104585121B CN201410804685.5A CN201410804685A CN104585121B CN 104585121 B CN104585121 B CN 104585121B CN 201410804685 A CN201410804685 A CN 201410804685A CN 104585121 B CN104585121 B CN 104585121B
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- China
- Prior art keywords
- enzyme
- filler
- aeration
- denitrogenation
- purifying box
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 133
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 title claims abstract description 120
- 241000251468 Actinopterygii Species 0.000 title claims abstract description 99
- 229910052757 nitrogen Inorganic materials 0.000 title claims abstract description 60
- 238000005273 aeration Methods 0.000 title claims abstract description 46
- 238000000034 method Methods 0.000 title claims description 21
- 238000009395 breeding Methods 0.000 title abstract description 11
- 230000001488 breeding effect Effects 0.000 title abstract description 11
- 239000003610 charcoal Substances 0.000 claims abstract description 105
- 238000012856 packing Methods 0.000 claims abstract description 16
- 239000000945 filler Substances 0.000 claims description 124
- 102000004190 Enzymes Human genes 0.000 claims description 119
- 108090000790 Enzymes Proteins 0.000 claims description 119
- 229940088598 enzyme Drugs 0.000 claims description 119
- 239000003795 chemical substances by application Substances 0.000 claims description 34
- 238000012258 culturing Methods 0.000 claims description 32
- 239000007788 liquid Substances 0.000 claims description 31
- 235000017166 Bambusa arundinacea Nutrition 0.000 claims description 28
- 235000017491 Bambusa tulda Nutrition 0.000 claims description 28
- 241001330002 Bambuseae Species 0.000 claims description 28
- 235000015334 Phyllostachys viridis Nutrition 0.000 claims description 28
- 239000011425 bamboo Substances 0.000 claims description 28
- 238000005276 aerator Methods 0.000 claims description 21
- 238000005507 spraying Methods 0.000 claims description 16
- 230000008859 change Effects 0.000 claims description 14
- DLRVVLDZNNYCBX-UHFFFAOYSA-N Polydextrose Polymers OC1C(O)C(O)C(CO)OC1OCC1C(O)C(O)C(O)C(O)O1 DLRVVLDZNNYCBX-UHFFFAOYSA-N 0.000 claims description 12
- 239000002893 slag Substances 0.000 claims description 12
- 239000001888 Peptone Substances 0.000 claims description 11
- 108010080698 Peptones Proteins 0.000 claims description 11
- 235000019319 peptone Nutrition 0.000 claims description 11
- 108010059892 Cellulase Proteins 0.000 claims description 10
- 229940106157 cellulase Drugs 0.000 claims description 10
- 239000002245 particle Substances 0.000 claims description 9
- 230000000249 desinfective effect Effects 0.000 claims description 8
- 239000000463 material Substances 0.000 claims description 8
- 238000002156 mixing Methods 0.000 claims description 8
- 238000000605 extraction Methods 0.000 claims description 7
- 238000012216 screening Methods 0.000 claims description 7
- 230000003068 static effect Effects 0.000 claims description 7
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 claims description 6
- 229920001100 Polydextrose Polymers 0.000 claims description 6
- 230000001546 nitrifying effect Effects 0.000 claims description 6
- 239000001259 polydextrose Substances 0.000 claims description 6
- 235000013856 polydextrose Nutrition 0.000 claims description 6
- 229940035035 polydextrose Drugs 0.000 claims description 6
- MTDHILKWIRSIHB-UHFFFAOYSA-N (5-azaniumyl-3,4,6-trihydroxyoxan-2-yl)methyl sulfate Chemical compound NC1C(O)OC(COS(O)(=O)=O)C(O)C1O MTDHILKWIRSIHB-UHFFFAOYSA-N 0.000 claims description 5
- 108091005804 Peptidases Proteins 0.000 claims description 5
- 229960002849 glucosamine sulfate Drugs 0.000 claims description 5
- 239000004365 Protease Substances 0.000 claims description 4
- 102100037486 Reverse transcriptase/ribonuclease H Human genes 0.000 claims description 4
- 230000000903 blocking effect Effects 0.000 claims description 4
- 229910000358 iron sulfate Inorganic materials 0.000 claims description 4
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 claims description 4
- 229910000402 monopotassium phosphate Inorganic materials 0.000 claims description 4
- 235000019796 monopotassium phosphate Nutrition 0.000 claims description 4
- PJNZPQUBCPKICU-UHFFFAOYSA-N phosphoric acid;potassium Chemical compound [K].OP(O)(O)=O PJNZPQUBCPKICU-UHFFFAOYSA-N 0.000 claims description 4
- 238000012545 processing Methods 0.000 claims description 4
- 210000000582 semen Anatomy 0.000 claims description 4
- CBOJBBMQJBVCMW-BTVCFUMJSA-N (2r,3r,4s,5r)-2-amino-3,4,5,6-tetrahydroxyhexanal;hydrochloride Chemical compound Cl.O=C[C@H](N)[C@@H](O)[C@H](O)[C@H](O)CO CBOJBBMQJBVCMW-BTVCFUMJSA-N 0.000 claims description 3
- 244000302661 Phyllostachys pubescens Species 0.000 claims description 3
- 235000003570 Phyllostachys pubescens Nutrition 0.000 claims description 3
- 240000004808 Saccharomyces cerevisiae Species 0.000 claims description 3
- 102000038379 digestive enzymes Human genes 0.000 claims description 3
- 108091007734 digestive enzymes Proteins 0.000 claims description 3
- 229960001911 glucosamine hydrochloride Drugs 0.000 claims description 3
- 229910052943 magnesium sulfate Inorganic materials 0.000 claims description 3
- 235000019341 magnesium sulphate Nutrition 0.000 claims description 3
- 239000004382 Amylase Substances 0.000 claims description 2
- 102000013142 Amylases Human genes 0.000 claims description 2
- 108010065511 Amylases Proteins 0.000 claims description 2
- 241000196324 Embryophyta Species 0.000 claims description 2
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 claims description 2
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims description 2
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims description 2
- 235000011130 ammonium sulphate Nutrition 0.000 claims description 2
- 235000019418 amylase Nutrition 0.000 claims description 2
- 238000001035 drying Methods 0.000 claims description 2
- 238000005086 pumping Methods 0.000 claims description 2
- 102000016938 Catalase Human genes 0.000 claims 1
- 108010053835 Catalase Proteins 0.000 claims 1
- 239000007789 gas Substances 0.000 claims 1
- 239000008103 glucose Substances 0.000 claims 1
- 125000002924 primary amino group Chemical group [H]N([H])* 0.000 claims 1
- 239000007921 spray Substances 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 22
- 210000003608 fece Anatomy 0.000 abstract description 4
- 238000004659 sterilization and disinfection Methods 0.000 abstract description 3
- 238000001179 sorption measurement Methods 0.000 abstract 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 18
- 244000005700 microbiome Species 0.000 description 16
- 241000252229 Carassius auratus Species 0.000 description 12
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 description 8
- 238000000746 purification Methods 0.000 description 6
- 230000004083 survival effect Effects 0.000 description 6
- 230000008569 process Effects 0.000 description 5
- 241000252233 Cyprinus carpio Species 0.000 description 4
- 238000003756 stirring Methods 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 3
- 235000019733 Fish meal Nutrition 0.000 description 3
- 241000720946 Hypophthalmichthys molitrix Species 0.000 description 3
- 230000009471 action Effects 0.000 description 3
- 229910052799 carbon Inorganic materials 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 238000000354 decomposition reaction Methods 0.000 description 3
- 238000011049 filling Methods 0.000 description 3
- 239000004467 fishmeal Substances 0.000 description 3
- 230000001737 promoting effect Effects 0.000 description 3
- 235000019419 proteases Nutrition 0.000 description 3
- 239000008399 tap water Substances 0.000 description 3
- 235000020679 tap water Nutrition 0.000 description 3
- 238000009423 ventilation Methods 0.000 description 3
- 239000002023 wood Substances 0.000 description 3
- MSWZFWKMSRAUBD-IVMDWMLBSA-N 2-amino-2-deoxy-D-glucopyranose Chemical compound N[C@H]1C(O)O[C@H](CO)[C@@H](O)[C@@H]1O MSWZFWKMSRAUBD-IVMDWMLBSA-N 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- MSWZFWKMSRAUBD-UHFFFAOYSA-N beta-D-galactosamine Natural products NC1C(O)OC(CO)C(O)C1O MSWZFWKMSRAUBD-UHFFFAOYSA-N 0.000 description 2
- 238000005352 clarification Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 238000013461 design Methods 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 229960002442 glucosamine Drugs 0.000 description 2
- 238000006396 nitration reaction Methods 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 235000020995 raw meat Nutrition 0.000 description 2
- VTEIFHQUZWABDE-UHFFFAOYSA-N 2-(2,5-dimethoxy-4-methylphenyl)-2-methoxyethanamine Chemical compound COC(CN)C1=CC(OC)=C(C)C=C1OC VTEIFHQUZWABDE-UHFFFAOYSA-N 0.000 description 1
- 101000906492 Arabidopsis thaliana Endoglucanase 1 Proteins 0.000 description 1
- 241000894006 Bacteria Species 0.000 description 1
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 1
- 108010093096 Immobilized Enzymes Proteins 0.000 description 1
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 1
- 231100000678 Mycotoxin Toxicity 0.000 description 1
- 102000035195 Peptidases Human genes 0.000 description 1
- 101001036014 Ruminiclostridium josui Endoglucanase 2 Proteins 0.000 description 1
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 230000002844 continuous effect Effects 0.000 description 1
- 238000005202 decontamination Methods 0.000 description 1
- 230000003588 decontaminative effect Effects 0.000 description 1
- 238000005034 decoration Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 108010091371 endoglucanase 1 Proteins 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000006911 enzymatic reaction Methods 0.000 description 1
- 230000029142 excretion Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 1
- 239000010931 gold Substances 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000007373 indentation Methods 0.000 description 1
- 230000006698 induction Effects 0.000 description 1
- 230000002045 lasting effect Effects 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 239000003607 modifier Substances 0.000 description 1
- 239000002636 mycotoxin Substances 0.000 description 1
- 239000005445 natural material Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 235000008935 nutritious Nutrition 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000032696 parturition Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000002062 proliferating effect Effects 0.000 description 1
- 235000019833 protease Nutrition 0.000 description 1
- 239000008213 purified water Substances 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 235000013547 stew Nutrition 0.000 description 1
- 239000001117 sulphuric acid Substances 0.000 description 1
- 235000011149 sulphuric acid Nutrition 0.000 description 1
- 230000001360 synchronised effect Effects 0.000 description 1
- 208000011580 syndromic disease Diseases 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
- A01K63/003—Aquaria; Terraria
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
- A01K63/04—Arrangements for treating water specially adapted to receptacles for live fish
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
- C02F9/20—Portable or detachable small-scale multistage treatment devices, e.g. point of use or laboratory water purification systems
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Marine Sciences & Fisheries (AREA)
- Animal Husbandry (AREA)
- Biodiversity & Conservation Biology (AREA)
- Clinical Laboratory Science (AREA)
- Health & Medical Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Biological Treatment Of Waste Water (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The invention provides an ecological fish tank for driving water circulation and removing total nitrogen through aeration. The ecological fish tank comprises an ultraviolet disinfection lamp tube, a bio-enzyme charcoal packing purifying box, a denitrification nitrogen removal packing purifying box and a breeding tank. The ultraviolet disinfection lamp tube is arranged at the bottom of the denitrification nitrogen removal packing purifying box. The bio-enzyme charcoal packing purifying box is formed by bio-enzyme charcoal packing and an aeration device. The denitrification nitrogen removal packing purifying box is formed by denitrification nitrogen removal packing and an aeration device. A water outlet above the bio-enzyme charcoal packing purifying box and a water outlet above the denitrification nitrogen removal packing purifying box are lower the water face of a water body in the breeding tank. Under the effects of the aeration devices, the water body in the lower portion of the breeding tank enters the upper portion of the breeding tank through the bio-enzyme charcoal packing and the denitrification nitrogen removal packing from bottom to top. The ecological fish tank has the capacity of efficiently decomposing fish feces and purifying the water quality, and has the high adsorption capacity; the fish feces and feed left at the bottom of the facility are effectively removed, it is guaranteed that the quality of water in the breeding tank is clean, and water changing is not needed.
Description
Technical field
The present invention relates to a kind of fish jar, more particularly, to a kind of aeration driving water circulation and removal total nitrogen ecological fish bowl and use
The method of its foster edible fish.
Background technology
Fish is nutritious, and that eats is delicious.But the change due to water environment pollution and breeding way method, people generally sigh with feeling
Now it is difficult to experience the delicious food of the past ichthyophagy.Simultaneously with the raising of people's living standard, ornamental fish tank is as a kind of decoration
Used in market, office and family by increasing.However, because fish jar is the closing water body of a very little, being also
One unstable dynamic water body, the feces of the feedstuff of input and Fish itself, make the ammonia nitrogen in water, nitrite nitrogen, with
And the concentration of total nitrogen constantly raises, water quality constantly deteriorates.For solving the problems, such as " water ", market has some to pass through physical filtering, change
Learn the device that the methods such as filtration solve fish tank water, remain a need for often cleaning, although nitrifier thrown in by some aquariums,
Decrease the content of ammonia nitrogen and nitrite nitrogen, but still cannot remove nitric nitrogen and total nitrogen, with nitric nitrogen with always
The accumulation of nitrogen, the pH of fish jar water quality is gradually lowered, and have impact on life habit and the eating mouth feel of fish, for this current fish jar is
For supporting the fish viewed and admired, edible fish supported by rarely seen utilization family fish jar.
Content of the invention
It is an object of the invention to provide the aeration that a kind of structure is simple and energy consumption is low drives water circulation and removes total nitrogen life
State fish jar and the method using its foster edible fish.
The present invention by solving the scheme that adopted of above-mentioned technical problem is:
A kind of aeration drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that it includes ultraviolet disinfecting tube, life
Thing enzyme Linesless charcoal filler purifying box, denitrification denitrogenation filler purifying box and culturing jar;Described enzyme Linesless charcoal filler purifying box and anti-
Nitrification denitrogenation filler purifying box is separately positioned on the both sides of culturing jar, and it is net that described ultraviolet disinfecting tube is placed in denitrification denitrogenation filler
Change the bottom of case:Described enzyme Linesless charcoal filler purifying box by enzyme Linesless charcoal filler and is arranged at below enzyme Linesless charcoal filler
Aerator constitute;Described denitrification denitrogenation filler purifying box by denitrification denitrogenation filler and is arranged at denitrification denitrogenation filler
The aerator of lower section is constituted;On outlet and denitrification denitrogenation filler purifying box above described enzyme Linesless charcoal filler purifying box
Square outlet is below the water surface elevation of culturing jar water body;In the presence of aerator, the water body of culturing jar bottom by down to
On respectively through the top entering into culturing jar after enzyme Linesless charcoal filler and denitrification denitrogenation filler.
In such scheme, the aerator of described enzyme Linesless charcoal filler purifying box is to continue aeration;Described denitrification takes off
The aerator of nitrogen filler purifying box is interval aeration.
In such scheme, described aeration drives water circulation also to include at least one residue with removal total nitrogen ecological fish bowl and collects
Device, each crumbs collector includes being arranged on the funnel shaped poly- slag chute of culturing jar bottom, umbellate form vortex accelerates baffle plate and
Residue extraction pipeline, it is zigzag that described umbellate form vortex accelerates the base of baffle plate, described umbellate form vortex accelerate the base of baffle plate with described
Contact and have residue excretion slot between the inwall of poly- slag chute, the slag-drip opening of described poly- slag chute is connected with Residue extraction pipeline.
In such scheme, described enzyme Linesless charcoal filler is prepared by following methods:
1) the natural Linesless charcoal through vibration screening and rounding, add modifying agent in the way of spraying, natural Charcoal Weight
Part by weight with modifying agent is 3:1, described modifying agent includes A liquid and B liquid:Described A liquid includes 1-5% by weight percentage
Any one or a few mixed in glucosamine, 1-5% glucosamine hydrochloride and 0.5-4% glucosamine sulfate
Close, balance of water, that described A liquid each group is divided and be 100%;Described B liquid includes 5-20% Semen Maydis pulp, 4- by weight percentage
20% peptone, 0.5-3% ammonium sulfate, 0.1-2% iron sulfate, 0.1-2% potassium dihydrogen phosphate, 0.1-2% magnesium sulfate and 1-5%
Yeast in any one or a few mixing, balance of water, that described B liquid each group is divided and be 100%;
2) static after adding enzyme agent and being sufficiently stirred for, the addition of enzyme agent is 1 with the mass ratio of natural Linesless charcoal:(1000-
2000), enzyme agent includes 2-20% pectase, 5-20% protease, 5-20% Digestive Enzyme, 5-25% cellulase, 5-20% mistake
Any one or a few mixing in hydrogen oxide enzyme and 5-20% amylase, balance of water is that described enzyme agent each group is divided and be
100%;
3) after using negative-pressure vacuum pumping vacuum, aeration-drying, it is eventually fabricated the enzyme Linesless charcoal that water content is 8-10%
Filler.
In such scheme, the volume ratio of described A liquid and B liquid is 1:(0.5-1.2).
In such scheme, described natural Linesless charcoal be through the broad-leaf forest of 800-1200 DEG C of high temperature cabonization, Coniferous forest branch or
Bamboo root root and stem of certain plants char-forming material.
In such scheme, described step 1) in the particle diameter of Linesless charcoal after rounding be 6-20mm.
In such scheme, described step 1) in sieve be that a natural charcoal particle is led to vibration screening machine, control nature wood
Between charcoal particle diameter 5cm-25cm.
In such scheme, the denitrogenation filler in described denitrogenation packing layer is made up of bamboo piece and denitrogenation Enzyme reactors, described
Denitrogenation Enzyme reactors include polydextrose, peptone, cellulase, nitrifying ferment and denitrification enzyme.
In such scheme, the denitrogenation filler in described denitrogenation packing layer is prepared by following methods:The bamboo through processing
It is 8 that piece adds denitrogenation Enzyme reactors, bamboo piece and denitrogenation Enzyme reactors weight ratio in the way of spraying:1, described denitrogenation enzyme is combined
Agent includes 1-5% polydextrose, 3-10% peptone, 2-20% cellulase, 5-30% nitrifying ferment, 5-30% denitrification enzyme
Mixing, balance of water, that described denitrogenation Enzyme reactors each group is divided and be 100%;Described bamboo piece is the Bamboo through blocking
Piece, bamboo chip is thickness 8-15mm, width 10-20mm, length 20-30mm.
The cleaning principle of the ecology of the present invention is:The special space structure being had using Linesless charcoal and huge specific surface area,
By promoting reaction control agent in Linesless charcoal surface spraying high molecular polymer surface modifier and microbial enzyme, and entered by negative pressure
Enter to inside filler, the negative charge on neutralization and shielding Linesless charcoal surface and micropore tube wall, create microorganism on Linesless charcoal surface and
The quick attachment of internal micropore tube wall and prolific ecological environment, provide carrier for immobilized enzyme simultaneously.Described fixation
Changing zymotechnic is interpolation enzyme in the state of negative pressure, by the physical absorption of Linesless charcoal and high molecular polymer ionic bond with altogether
The combination of valence link, is fixed on required multiple enzyme on Linesless charcoal filler, and induction specified microorganisms bacterium colony enters Linesless charcoal filler
Micropore inside carry out enzymatic reaction, keep the activity of microorganism, improve treatment effeciency and the effect of reactor.
The cleaning principle of the denitrogenation filler of the present invention is:Using bamboo piece, there is performance more than 80~100 for the C/N,
Can be to carry out denitrification reaction in this layer constantly to provide carbon source.By spraying denitrogenation compound enzyme agent on bamboo piece surface, allow poly- Portugal
Grape sugar and the combination of peptone and cellulase, nitrifying ferment and denitrification enzyme, cellulase, nitrifying ferment and denitrification enzyme
Stick to bamboo piece surface, the microorganism of induced decomposition cellulose and the microorganism of nitrification and denitrification are bred on bamboo piece
Growth.Because denitrogenation packing groove is in the state of intermittent aerating, the nitric nitrogen generating in enzyme Linesless charcoal stuffing box enters into
Carry out denitrification denitrogenation reaction, thus reaching the effect removing nitric nitrogen and total nitrogen after denitrogenation filler.
The invention has the beneficial effects as follows:
1) present invention, by the power as whole fish bowl circulating water for the aeration, the construction featuress using fish jar, allows in fish jar
Overall water circulation flows, and reduces power consumption.Using ecological filler, the energy there is efficient-decomposition fish excrement, purifying water
Power, keeps water quality clean.By the construction featuress of crumbs collector, form vortex and lateral pressure, promote to collect and remove not
The fish excrement that can decompose and food-residue ability, reduce equipment and energy consumption.
2) the ecological packing material of the present invention is all retrieved from the natural material of nature, is natural, safe;Water
Body microorganism, based on beneficial water microorganism, is from tap water, the microorganism of Fish itself, is natural, safe;Micro- life
Thing, while absorption, decomposing pollutant, had both purified water quality, enhanced the activity of water again, and synchronous realization is harnessed the river and foster water is double
Effect.Inventor has been carried out excess syndrome experiment more than a year to the efficacy effect of ecological filler purifying box, and result is:Fish jar water body PH
For a long time between 7-8.In sum, the innovative point of this filler is with self renewal purification function, being capable of digest and decompose automatically
Mud, can be continuously using more than 20 years.The ability have efficient-decomposition fish excrement, purifying water, has extremely strong absorbability, has
The fish excrement of effect removing facility bottom residual and feedstuff are it is ensured that culturing jar water quality is totally it is not necessary to change water.
Brief description
Fig. 1 drives water circulation for aeration and removes the perspective view of total nitrogen ecological fish bowl.
Fig. 2 is the front view of Fig. 1.
Fig. 3 accelerates the structural representation of baffle plate for the poly- slag chute in Fig. 1 and umbellate form vortex.
In figure, 1- ultraviolet disinfecting tube, 2- enzyme Linesless charcoal filler purifying box, 3- denitrification denitrogenation filler purifying box, 4-
Culturing jar, 5- crumbs collector, 6- enzyme Linesless charcoal filler, 7- denitrification denitrogenation filler, the poly- slag chute of 8-, 9- umbellate form vortex adds
Speed gear plate, 10- enzyme Linesless charcoal body filler purifies upper box part and crosses the mouth of a river, and 11- denitrification denitrogenation purifies upper box part and crosses the mouth of a river, 12-
Stand frame, 13- filler filter, 14,15- exhaust-valves, 16- aerator, 17- aeration blower, 18- fish jar bottom filter, 19-
Residue extraction pipeline.
Specific embodiment
Below in conjunction with drawings and Examples, the present invention will be described further, but present disclosure is not limited solely to
The following examples.
Embodiment 1
As shown in Figure 1 to Figure 3, it drives water circulation for a kind of aeration that the embodiment of the present invention 1 provides and removes total nitrogen life
State fish jar, it includes ultraviolet disinfecting tube 1, enzyme Linesless charcoal filler purifying box 2, denitrification denitrogenation filler purifying box 3, culturing jar
4 and two crumbs collectors 5.Enzyme Linesless charcoal filler purifying box 2 and denitrification denitrogenation filler purifying box 3 are separately positioned on foster
Grow the both sides of cylinder 4.
Ultraviolet disinfecting tube 1 is used for water body is carried out disinfection.In the present embodiment, ultraviolet disinfecting tube 14 is placed in denitrification
Denitrogenation purifying box 3 bottom.
It is filled with enzyme Linesless charcoal filler 6 and aerator 16 in enzyme Linesless charcoal filler purifying box 2.In the present embodiment
In, the netted plastic bag of enzyme Linesless charcoal filler 6 is divided into several bags and is placed on stand frame 12.Aerator 16 is arranged at biology
Below enzyme Linesless charcoal filler 6.In the present embodiment, aerator 16 continuous aeration in enzyme Linesless charcoal filler purifying box 2, due to
The dynamic action that during aeration, bubble rises, drives the water body of enzyme Linesless charcoal filler purifying box 2 to move across biology from lower to upper
Enzyme Linesless charcoal filler 6, reaches the effect removing water pollution material.In the present embodiment, below enzyme Linesless charcoal filler purifying box 2
It is connected with culturing jar 4, the water surface elevation that the mouth of a river 10 is less than culturing jar 4 water body is crossed in the top of enzyme Linesless charcoal filler purifying box 2,
The water of the clean clarification purifying through enzyme Linesless charcoal filler 6 enters in culturing jar 4 by outlet 10, dynamic in lasting aeration
Under power effect, the water body of culturing jar 4, constantly through being purified and Circulation by enzyme Linesless charcoal filler 6, is reached and holds
The continuous effect effectively removing polluter in culturing jar 4 water body.
It is filled with denitrification denitrogenation filler 7 and aerator 16 in denitrification filler purifying box 3.In the present embodiment, instead
The nitrification netted plastic bag of denitrogenation filler 7 is divided into several bags and is placed on stand frame 12.Aerator 16 is arranged at denitrification and takes off
Below nitrogen filler 7.In the present embodiment, the indirect aeration of aerator 16 in denitrification denitrogenation filler purifying box 2, every 6 little
When aeration 20 minutes, the dynamic action being risen due to bubble during aeration, drive the water body of denitrification denitrogenation filler purifying box 3 by under
Up move across denitrification denitrogenation filler 7, reach the effect that denitrification removes water body total nitrogen.In the present embodiment, denitrification
Denitrogenation filler purifying box 3 lower section is connected with culturing jar 4, and the mouth of a river 11 is crossed less than foster in the top of denitrification denitrogenation filler purifying box 3
Grow the water surface elevation of cylinder 4 water body, the water of the clean clarification purifying through denitrification denitrogenation filler 7 passes through outlet 11 and enters cultivation
In cylinder 4, under the dynamic action of aeration, the water body of culturing jar 4 is constantly purified through denitrification denitrogenation filler 6 and is circulated
Effect, reaches and effectively carries out anti-nitration reaction, removes the effect of culturing jar water body total nitrogen.
Two crumbs collectors 5 are arranged on culturing jar 4 bottom, for collecting enzyme Linesless charcoal filler and denitrification respectively
Mud and fish meal residue that denitrogenation filler produces in purification process.In the present embodiment, each crumbs collector 5 includes
It is arranged on the funnel shaped poly- slag chute 8 of culturing jar 4 bottom, umbellate form vortex accelerates baffle plate 9 and Residue extraction pipeline 19.The poly- slag chute of infundibulate
8 funnel-shaped design is in order that the activated sludge producing more easily concentrates on bottom to clear up, and umbellate form vortex accelerates
Baffle plate 9 base is zigzag design, and the inwall of base slag chute 8 poly- with infundibulate contacts, by periodically opening emptying
Valve 14 and 15, is vortexed, in the inwall of the poly- slag chute of infundibulate 5 and umbellate form, residue and the fish feces accelerating baffle plate 9 gathering, in culturing jar
Under lateral pressure and eddy current effect that water body gravity is formed, sink and pass through Residue extraction pipeline 19 to discharging from indentation rapidly.
This aeration drives water circulation and with the work process removing total nitrogen ecological fish bowl is:Produce in the aeration of aerator 16
Under rising bubble effect, the water of enzyme Linesless charcoal filler purifying box 2 bottom from the bottom to top through enzyme Linesless charcoal filler 6, due to
Enzyme Linesless charcoal filler 6 has to COD, and the purification function such as BOD and ammonia nitrogen and nitrite nitrogen, for this water body through enzyme
Clean water after Linesless charcoal filler 6 purifies enters into culturing jar 4, not by enzyme Linesless charcoal filler purifying box 2 upper outlet 10
Under disconnected aeration effect, above-mentioned purification process constantly circulates, and has reached the purpose to cultivation fish tank water body purification, particularly logical
Cross aeration, not only increase the dissolved oxygen of water body, by circularly purifying repeatedly, in the presence of enzyme Linesless charcoal filler 6, be handle
The nitric nitrogen less to fish survival effect is all oxidized to the maximum ammonia nitrogen of fish survival effect and nitrite nitrogen.In culturing jar
Also there is same decontamination cycle process in the denitrification denitrogenation filler purifying box 3 of 4 other sides, except for the difference that denitrification denitrogenation is filled out
The aerator 16 of material purifying box 3 is to adopt intermittent aeration, forms denitrifying anaerobic state, on anti-digestion denitrogenation filler
Denitrification denitrogenation microorganism in the presence of carry out anti-nitration reaction.Aeration in the present embodiment adopts aeration blower, is giving birth to
The aerator of thing enzyme Linesless charcoal filler purifying box continues aeration as the power of fish jar water circulation;Denitrification denitrogenation filler purifies
The aerator of case passes through to connect the Control intermittent aerating time, reaches anti-digestion denitrogenation, the function of preventing and treating total nitrogen accumulation.
In the present embodiment, enzyme Linesless charcoal filler is prepared by following methods:
The Linesless charcoal of the particle diameter 6-20mm through vibration screening and rounding, in the way of spraying, add Charcoal Weight
Glucosamine sulfate 4% in the A liquid of 30% modifying agent, wherein modifying agent, balance of water.Semen Maydis pulp 8%, sulphuric acid in B liquid
Ferrum 0.1%, magnesium sulfate 0.1%, yeast 1%, balance of water, the main nutrient that microorganism is provided of effect of B liquid.A liquid and B liquid
After mixing, the surface charge for changing Linesless charcoal serves, with the breeding promoting to fix enzyme and promotion microorganism, the effect being multiplied
Really.The process of spraying stirs Linesless charcoal, and the time stirred of spraying is 15 minutes, adds enzyme agent, the addition of enzyme agent after static 30 minutes
Amount is the 1/1000 of Charcoal Weight, and enzyme agent includes pectase 15%, protease 5%, balance of water.It is sufficiently stirred for static 15 minutes
Afterwards, after using 30 minutes evacuation of negative-pressure vacuum pump (75KPa), ventilation dries up, and is eventually fabricated the enzyme wood that water content is 8%
Carbon filling material.
In the present embodiment, denitrification denitrogenation filler is prepared by following methods:
Bamboo piece through processing is added denitrogenation Enzyme reactors, bamboo piece and denitrogenation Enzyme reactors weight in the way of spraying
Amount ratio is 8:1, described denitrogenation Enzyme reactors include 2% polydextrose, 5% peptone, 5% cellulase and 5% denitrification
Enzyme, balance of water, that described denitrogenation Enzyme reactors each group is divided and be 100%;Described bamboo piece is through blocking Phyllostachys pubescens Mazei ex H.de Lebaie bamboo chip, bamboo
Piece is thickness 8-15mm, width 10-20mm, length 20-30mm.
By the contrast applicable cases in 3 fish jar filling difference fillers it was demonstrated that enzyme Linesless charcoal filler and denitrification take off
The purification to water quality for the nitrogen filler.The volume of 3 fish jars is identical with shape, and fish jar is in enzyme Linesless charcoal stuffing box and anti-
Nitrification denitrogenation stuffing box does not all put filler, and as blank, No. two fish jars are in enzyme Linesless charcoal stuffing box equipped with biology
0.1 cubic metre of enzyme Linesless charcoal filler, does not fill denitrification denitrogenation filler in denitrification denitrogenation stuffing box.No. three fish jars are the present embodiment
The fish jar protected, that is, in enzyme Linesless charcoal stuffing box equipped with 0.1 cubic metre of enzyme Linesless charcoal filler, in denitrification denitrogenation filler
Case is equipped with 0.1 cubic metre of denitrification denitrogenation filler.No. one, No. two volumes with No. three fish jars identical, be 1 cubic metre, three fishes
Cylinder equally cultivates Carassius auratuses 20, and in 7 months, cultivation period three fish jar does not all change water, is only regular addition at aeration
The tap water of reason.The COD of number fish jar (do not filled out what a filler laissez-faire) water quality, ammonia nitrogen, total values of nitrogen might increase 58.5% respectively,
995%th, 43.5%, water is muddy, and color becomes dark brown, and transparency drops to 50 from 80cm, shows that the polluter of this water body is continuous
Increase, change of water quality, Carassius auratuses are also dead month by month, it is 75% that the Carassius auratuses in 7 months have survived;No. two fish jars (are only filled out and are put enzyme
Linesless charcoal filler) COD of water quality and the value kept stable of ammonia nitrogen, also there are about reducing, COD and ammonia nitrogen reduce 9% He respectively
10%, the total nitrogen of No. two fish jars slightly raises in 7 months periods value, although total values of nitrogen might increases 22.9%, with a fish jar
Total nitrogen increasing degree (43.5%) compare, only the 47% of a fish jar increasing degree, show that enzyme Linesless charcoal goes to total nitrogen
The ability removed not is very high.Transparent through No. two fish jar water quality of the cultivation Carassius auratuses of 7 months, water color does not change,
The survival rate of Carassius auratuses reaches 100%.Show that enzyme Linesless charcoal filler has obvious removal ability, to total to COD and ammonia nitrogen
The clearance of nitrogen is relatively low.No. three fish jars (fill out simultaneously and put enzyme Linesless charcoal filler and denitrification denitrogenation filler) were in the cultivation of 7 months
The COD of its water quality of period, the rate of descent of ammonia nitrogen and total values of nitrogen might is 15%, 45.4% and 24% respectively.Through the cultivation gold of 7 months
No. three fish jar water quality of fish are transparent, and water color does not change, and the survival rate of Carassius auratuses reaches 100%.The result of No. three fish jars
Show to fill out the fish jar putting enzyme Linesless charcoal filler and denitrification denitrogenation filler simultaneously, not only there is the ability removing water quality total nitrogen,
Also improve the removal ability to COD and ammonia nitrogen.
Three fish jar fish jar water quality indices during cultivation in 7 months are as follows;
Embodiment 2
The present embodiment is roughly the same with No. three fish jar in embodiment 1, difference be enzyme Linesless charcoal filler by
Prepared by following methods:
The Linesless charcoal of the particle diameter 6-20mm through vibration screening and rounding, in the way of spraying, add Charcoal Weight
Glucosamine 1% in the A liquid of 30% modifying agent, wherein modifying agent, glucosamine sulfate 3%, balance of water.In B liquid
Peptone 8%, iron sulfate 0.1%, potassium dihydrogen phosphate 0.1%, balance of water, the main nutrition that microorganism is provided of effect of B liquid
Agent.After A liquid is mixed with B liquid, for changing the surface charge of Linesless charcoal and promoting fixing enzyme and promote the breeding of microorganism to rise
Arrive the effect being multiplied.The process of spraying stirs Linesless charcoal, and the time stirred of spraying is 15 minutes, adds enzyme after static 30 minutes
Agent, the addition of enzyme agent is the 1/1000 of Charcoal Weight, and enzyme agent includes proteinase 8 %, cellulase 1%, balance of water.Fully
After stirring static 15 minutes, after 30 minutes evacuation of negative-pressure vacuum pump (75KPa), ventilation dries up, and is eventually fabricated water content
Enzyme Linesless charcoal filler for 8%.
In the present embodiment, denitrification denitrogenation filler is prepared by following methods:
Bamboo piece through processing is added denitrogenation Enzyme reactors, bamboo piece and denitrogenation Enzyme reactors weight in the way of spraying
Amount ratio is 8:1, described denitrogenation Enzyme reactors include 5% polydextrose, 10% peptone, 5% cellulase and 8% anti-nitre
Change enzyme, balance of water, that described denitrogenation Enzyme reactors each group is divided and be 100%;Described bamboo piece is through blocking Phyllostachys pubescens Mazei ex H.de Lebaie bamboo chip,
Bamboo chip is thickness 8-15mm, width 10-20mm, length 20-30mm.
In the present embodiment, apparatus of the present invention are used for cultivating Carassius auratuss and Cyprinus carpio L..Culturing jar water body volume is 1 cube, enzyme
The usage amount of Linesless charcoal filler is 0.1 cube, and denitrification denitrogenation filler usage amount is 0.1 cube, cultivates Carassius auratuss 10, Cyprinus carpio L. 10
Bar, does not change water within 5 months periods of culturing time, the tap water that simply regular replenishment is tamed through aeration, and according to fish
Quantity timing throw in fish meal.During cultivating, COD in fish tank water, ammonia nitrogen, nitrite nitrogen and total values of nitrogen might are substantially steady
Fixed, the total nitrogen of wherein fish jar water body reduces 13%, COD and reduces 9.4%, and ammonia nitrogen reduces 18%, and the transparency of water keeps
In more than 100cm, the survival rate of fish is 100%.This shows to fill out simultaneously puts enzyme Linesless charcoal filler and denitrification denitrogenation filler
Fish jar, has the ability removing water quality total nitrogen, not only effectively prevents total nitrogen from accumulating, and also improves and goes decapacitation to COD and ammonia nitrogen
Power.
The present embodiment fish jar fish jar water quality indices during cultivation in 5 months are as follows;
1 month | 2 months | 3 months | 5 months | |
COD(mg/l) | 35.3 | 30.2 | 31 | 32 |
Ammonia nitrogen (mg/l) | 0.32 | 0.34 | 0.23 | 0.26 |
Nitrite nitrogen (mg/l) | 0.08 | 0.05 | 0.10 | 0.10 |
Total nitrogen (mg/l) | 15 | 13 | 14 | 13 |
Transparency (cm) | >100 | >100 | >100 | >100 |
Carassius auratuses existence number (bar) | 20 | 20 | 20 | 20 |
Embodiment 3
The present embodiment is roughly the same with No. three fish jar in embodiment 1, difference be enzyme Linesless charcoal filler by
Prepared by following methods:
The Linesless charcoal of the particle diameter 6-20mm through vibration screening and rounding, in the way of spraying, add Charcoal Weight
Glucosamine hydrochloride 1.5% in the A liquid of 30% modifying agent, wherein modifying agent, glucosamine sulfate 1.2%, balance of
Water.Semen Maydis pulp 5% in B liquid, peptone 4%, iron sulfate 0.1%, potassium dihydrogen phosphate 0.1%, balance of water, the effect master of B liquid
The nutrient of microorganism to be provided.After A liquid is mixed with B liquid, for change Linesless charcoal surface charge and promote fixing enzyme and
The breeding of promotion microorganism serves the effect of multiplication.The process of spraying stirs Linesless charcoal, and the time stirred of spraying is 15 minutes, quiet
Only add enzyme agent after 30 minutes, the addition of enzyme agent is the 1/1000 of Charcoal Weight, and enzyme agent includes protease 6%, Digestive Enzyme
2%, cellulase 2%, balance of water.After being sufficiently stirred for static 15 minutes, taken out within 30 minutes very using negative-pressure vacuum pump (75KPa)
After sky, ventilation dries up, and is eventually fabricated the enzyme Linesless charcoal filler that water content is 8%.
In the present embodiment, fish jar of the present invention is used for cultivating Carassius auratuss, Cyprinus carpio L. and Hypophthalmichthys molitrix.Culturing jar water body volume is 1.5 cubes,
The usage amount of enzyme Linesless charcoal filler is 0.12 cube, and denitrification denitrogenation filler usage amount is 0.21 cube, cultivates Carassius auratuss 10,
Cyprinus carpio L. 6 and Hypophthalmichthys molitrix 6, during 5 months of culturing time in do not change water, simply regular replenishment tame through aeration oneself
Water, and throw in fish meal according to the quantity timing of fish.During cultivating, COD in fish tank water, ammonia nitrogen, nitrite nitrogen and
Total values of nitrogen might is basicly stable simultaneously, and 26.6%, the COD that reduces of the wherein total nitrogen of fish jar water body reduces 20%, and ammonia nitrogen reduces
32.1%, the transparency of water is maintained at more than 100cm, and the survival rate of fish is 100%.This example shows to fill out simultaneously puts enzyme wood
Carbon filling material and the fish jar of denitrification denitrogenation filler, have the ability removing water quality total nitrogen, not only effectively prevent total nitrogen from accumulating, also carry
The high removal ability to COD and ammonia nitrogen.
The present embodiment fish jar water quality indices during cultivation in 5 months are as follows;
1 month | 2 months | 3 months | 5 months | |
COD(mg/l) | 36.3 | 40.2 | 38 | 28.8 |
Ammonia nitrogen (mg/l) | 0.28 | 0.22 | 0.23 | 0.19 |
Nitrite nitrogen (mg/l) | 0.09 | 0.05 | 0.1 | 0.1 |
Total nitrogen (mg/l) | 15 | 13 | 12 | 11 |
Transparency (cm) | >100 | >100 | >100 | >100 |
Carassius auratuses existence number (bar) | 22 | 22 | 22 | 22 |
Embodiment 4
The present embodiment also provides a kind of method that edible fish supported by fish jar of use embodiment 1 or 2 or 3, comprises the following steps:
1) support good water with a period of time in advance before breeding fish using described fish jar, Primary Reference index needs to meet:A.pH protects
Hold between 7-8;B. effective microorganisms account for 85%;C. clarity is good;D. Mycotoxin identification goes to zero;
2) thrown again using the saline soak 15-20 minute of 30% concentration before the edible fish bought from market being put into fish jar
Enter fish jar to raise;
3) put into raise fish cultivate more than 15 days in the good water of fish jar, by good water removal breed in stew left drug,
The taste of native raw meat mud raw meat is edible.
Claims (10)
1. a kind of aeration drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that it includes ultraviolet disinfecting tube, biology
Enzyme Linesless charcoal filler purifying box, denitrification denitrogenation filler purifying box and culturing jar;Described enzyme Linesless charcoal filler purifying box and anti-nitre
Change the both sides that denitrogenation filler purifying box is separately positioned on culturing jar, described ultraviolet disinfecting tube is placed in denitrification denitrogenation filler and purifies
The bottom of case:Described enzyme Linesless charcoal filler purifying box by enzyme Linesless charcoal filler and is arranged at below enzyme Linesless charcoal filler
Aerator is constituted;Described denitrification denitrogenation filler purifying box by denitrification denitrogenation filler and is arranged under denitrification denitrogenation filler
The aerator of side is constituted;Above outlet and denitrification denitrogenation filler purifying box above described enzyme Linesless charcoal filler purifying box
Outlet is below the water surface elevation of culturing jar water body;In the presence of aerator, the water body of culturing jar bottom is from the bottom to top
Respectively through the top entering into culturing jar after enzyme Linesless charcoal filler and denitrification denitrogenation filler.
2. aeration as claimed in claim 1 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described enzyme
The aerator of Linesless charcoal filler purifying box is to continue aeration;The aerator of described denitrification denitrogenation filler purifying box is that interval exposes
Gas.
3. aeration as claimed in claim 1 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described aeration drives
Dynamic water circulation also includes at least one crumbs collector with removing total nitrogen ecological fish bowl, and each crumbs collector includes arranging
Funnel shaped poly- slag chute in culturing jar bottom, umbellate form vortex accelerate baffle plate and Residue extraction pipeline, and described umbellate form vortex accelerates baffle plate
Base be zigzag, described umbellate form vortex accelerates to contact and have residue to arrange between the base of baffle plate and the inwall of described poly- slag chute
Let out slot, the slag-drip opening of described poly- slag chute is connected with Residue extraction pipeline.
4. aeration as claimed in claim 1 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described enzyme
Linesless charcoal filler is prepared by following methods:
1) the natural Linesless charcoal through vibration screening and rounding, by spray in the way of add modifying agent, natural Charcoal Weight with change
The part by weight of property agent is 3:1, described modifying agent includes A liquid and B liquid:Described A liquid includes 1-5% amino by weight percentage
Any one or a few mixing in glucose, 1-5% glucosamine hydrochloride and 0.5-4% glucosamine sulfate, surplus
For water, that described A liquid each group is divided and be 100%;Described B liquid includes 5-20% Semen Maydis pulp, 4-20% albumen by weight percentage
Appointing in peptone, 0.5-3% ammonium sulfate, 0.1-2% iron sulfate, the yeast of 0.1-2% potassium dihydrogen phosphate, 0.1-2% magnesium sulfate and 1-5%
Anticipate the mixing of one or more, balance of water is that described B liquid each group is divided and be 100%;
2) static after adding enzyme agent and being sufficiently stirred for, the addition of enzyme agent is 1 with the mass ratio of natural Linesless charcoal:(1000-2000),
Enzyme agent includes 2-20% pectase, 5-20% protease, 5-20% Digestive Enzyme, 5-25% cellulase, 5-20% catalase and 5-
Any one or a few mixing in 20% amylase, balance of water, that described enzyme agent each group is divided and be 100%;
3) after using negative-pressure vacuum pumping vacuum, aeration-drying, it is eventually fabricated the enzyme Linesless charcoal filler that water content is 8-10%.
5. aeration as claimed in claim 4 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described A liquid and B
The volume ratio of liquid is 1:(0.5-1.2).
6. aeration as claimed in claim 4 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described naturally wooden
Charcoal is through the broad-leaf forest of 800-1200 DEG C of high temperature cabonization, Coniferous forest branch or bamboo root root and stem of certain plants char-forming material.
7. aeration as claimed in claim 4 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described step 1)
The particle diameter of the Linesless charcoal after middle rounding is 6-20mm.
8. aeration as claimed in claim 4 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described step 1)
In to sieve be that a natural charcoal particle is led to vibration screening machine, control between nature charcoal particle diameter 5cm-25cm.
9. aeration as claimed in claim 1 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described denitrogenation is filled out
Denitrogenation filler in the bed of material is made up of bamboo piece and denitrogenation Enzyme reactors, and described denitrogenation Enzyme reactors include polydextrose, albumen
Peptone, cellulase, nitrifying ferment and denitrification enzyme.
10. aeration as claimed in claim 9 drives water circulation and removes total nitrogen ecological fish bowl it is characterised in that described denitrogenation
Denitrogenation filler in packing layer is prepared by following methods:Denitrogenation enzyme is added to be combined in the way of spraying the bamboo piece through processing
Agent, bamboo piece and denitrogenation Enzyme reactors weight ratio are 8:1, described denitrogenation Enzyme reactors include 1-5% polydextrose, 3-10% albumen
Peptone, 2-20% cellulase, 5-30% nitrifying ferment, the mixing of 5-30% denitrification enzyme, balance of water, described denitrogenation Enzyme reactors are each
Component sum is 100%;Described bamboo piece is the Phyllostachys pubescens Mazei ex H.de Lebaie bamboo chip through blocking, and bamboo chip is thickness 8-15mm, width 10-20mm, long
Degree 20-30mm.
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CN108541647B (en) * | 2016-05-16 | 2020-07-31 | 德化县丽德家居用品有限公司 | Fish tank |
CN107279031B (en) * | 2017-07-04 | 2023-10-27 | 浙江工商大学 | Device and method for purifying water in fish tank |
CN108094285A (en) * | 2017-12-18 | 2018-06-01 | 湖北海洋工程装备研究院有限公司 | Dead fish collector and dead fish collection device |
CN108821415A (en) * | 2018-07-02 | 2018-11-16 | 河南牧业经济学院 | A kind of mandarin fish breeding water produces the improver of water quality and preparation method thereof of cultivation |
CN111990323B (en) * | 2020-09-28 | 2023-09-29 | 珠海南方利洋水产科技有限公司 | Tail water treatment system of culture pond and construction method thereof |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5176100A (en) * | 1990-07-23 | 1993-01-05 | Okabe Co., Ltd. | Aquarium with closed water recirculatory system for culturing fish and shellfish |
CN201538728U (en) * | 2009-04-17 | 2010-08-04 | 北京工业大学 | Improved A2N denitrifying dephosphatation and deep denitrification device |
CN203256093U (en) * | 2013-05-12 | 2013-10-30 | 河北建设集团安装工程有限公司 | Sewage and wastewater advanced treatment system |
CN104094874A (en) * | 2014-04-01 | 2014-10-15 | 浙江省海洋开发研究院 | Industrial crab breeding system |
CN102923906B (en) * | 2012-10-24 | 2014-11-05 | 天津大学 | Campus landscape water-body water-quality maintaining and self-purifying system integrating functions of landscape and biological ecological restoration |
-
2014
- 2014-12-19 CN CN201410804685.5A patent/CN104585121B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5176100A (en) * | 1990-07-23 | 1993-01-05 | Okabe Co., Ltd. | Aquarium with closed water recirculatory system for culturing fish and shellfish |
CN201538728U (en) * | 2009-04-17 | 2010-08-04 | 北京工业大学 | Improved A2N denitrifying dephosphatation and deep denitrification device |
CN102923906B (en) * | 2012-10-24 | 2014-11-05 | 天津大学 | Campus landscape water-body water-quality maintaining and self-purifying system integrating functions of landscape and biological ecological restoration |
CN203256093U (en) * | 2013-05-12 | 2013-10-30 | 河北建设集团安装工程有限公司 | Sewage and wastewater advanced treatment system |
CN104094874A (en) * | 2014-04-01 | 2014-10-15 | 浙江省海洋开发研究院 | Industrial crab breeding system |
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