CN108069510A - A kind of solar anaerobic reactor assembly applied in natural water and its application method - Google Patents
A kind of solar anaerobic reactor assembly applied in natural water and its application method Download PDFInfo
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- CN108069510A CN108069510A CN201611020549.2A CN201611020549A CN108069510A CN 108069510 A CN108069510 A CN 108069510A CN 201611020549 A CN201611020549 A CN 201611020549A CN 108069510 A CN108069510 A CN 108069510A
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- water
- reaction kettle
- anaerobic reactor
- denitrifying bacteria
- solar
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- 238000000034 method Methods 0.000 title claims abstract description 45
- 239000008239 natural water Substances 0.000 title claims abstract description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 167
- 238000006243 chemical reaction Methods 0.000 claims abstract description 74
- 241000894006 Bacteria Species 0.000 claims abstract description 71
- 239000000463 material Substances 0.000 claims abstract description 27
- 239000000945 filler Substances 0.000 claims abstract description 26
- 238000005485 electric heating Methods 0.000 claims abstract description 23
- 230000001105 regulatory effect Effects 0.000 claims description 36
- 239000012190 activator Substances 0.000 claims description 20
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims description 16
- 230000004913 activation Effects 0.000 claims description 16
- 229920000642 polymer Polymers 0.000 claims description 16
- 238000010438 heat treatment Methods 0.000 claims description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 10
- 229910052751 metal Inorganic materials 0.000 claims description 10
- 239000002184 metal Substances 0.000 claims description 10
- 244000005700 microbiome Species 0.000 claims description 9
- 239000011780 sodium chloride Substances 0.000 claims description 9
- 210000000476 body water Anatomy 0.000 claims description 8
- 229910002651 NO3 Inorganic materials 0.000 claims description 7
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 claims description 7
- 230000001276 controlling effect Effects 0.000 claims description 7
- 239000007788 liquid Substances 0.000 claims description 7
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical group O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 6
- 238000011049 filling Methods 0.000 claims description 6
- 239000011229 interlayer Substances 0.000 claims description 6
- -1 polyethylene Polymers 0.000 claims description 6
- 239000002994 raw material Substances 0.000 claims description 6
- 150000003839 salts Chemical class 0.000 claims description 6
- 229920001817 Agar Polymers 0.000 claims description 5
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims description 5
- 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 5
- 239000001888 Peptone Substances 0.000 claims description 5
- 108010080698 Peptones Proteins 0.000 claims description 5
- 239000004372 Polyvinyl alcohol Substances 0.000 claims description 5
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 claims description 5
- VMHLLURERBWHNL-UHFFFAOYSA-M Sodium acetate Chemical compound [Na+].CC([O-])=O VMHLLURERBWHNL-UHFFFAOYSA-M 0.000 claims description 5
- 239000008272 agar Substances 0.000 claims description 5
- 229940041514 candida albicans extract Drugs 0.000 claims description 5
- 230000008859 change Effects 0.000 claims description 5
- 239000004615 ingredient Substances 0.000 claims description 5
- 235000019319 peptone Nutrition 0.000 claims description 5
- 229920002451 polyvinyl alcohol Polymers 0.000 claims description 5
- 239000001632 sodium acetate Substances 0.000 claims description 5
- 235000017281 sodium acetate Nutrition 0.000 claims description 5
- 239000012138 yeast extract Substances 0.000 claims description 5
- WQZGKKKJIJFFOK-VFUOTHLCSA-N beta-D-glucose Chemical compound OC[C@H]1O[C@@H](O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-VFUOTHLCSA-N 0.000 claims description 4
- 239000008103 glucose Substances 0.000 claims description 4
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 claims description 4
- 238000001556 precipitation Methods 0.000 claims description 4
- 239000000741 silica gel Substances 0.000 claims description 4
- 229910002027 silica gel Inorganic materials 0.000 claims description 4
- 238000001816 cooling Methods 0.000 claims description 3
- GUJOJGAPFQRJSV-UHFFFAOYSA-N dialuminum;dioxosilane;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3].O=[Si]=O.O=[Si]=O.O=[Si]=O.O=[Si]=O GUJOJGAPFQRJSV-UHFFFAOYSA-N 0.000 claims description 3
- RUTXIHLAWFEWGM-UHFFFAOYSA-H iron(3+) sulfate Chemical compound [Fe+3].[Fe+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O RUTXIHLAWFEWGM-UHFFFAOYSA-H 0.000 claims description 3
- 229910000360 iron(III) sulfate Inorganic materials 0.000 claims description 3
- 229910052901 montmorillonite Inorganic materials 0.000 claims description 3
- 239000001103 potassium chloride Substances 0.000 claims description 3
- 235000011164 potassium chloride Nutrition 0.000 claims description 3
- 238000003860 storage Methods 0.000 claims description 3
- 229910021578 Iron(III) chloride Inorganic materials 0.000 claims description 2
- 239000004743 Polypropylene Substances 0.000 claims description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 claims description 2
- 239000004411 aluminium Substances 0.000 claims description 2
- 229910052782 aluminium Inorganic materials 0.000 claims description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical group [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 2
- 239000001913 cellulose Substances 0.000 claims description 2
- 229920002678 cellulose Polymers 0.000 claims description 2
- 230000005611 electricity Effects 0.000 claims description 2
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims description 2
- 229920001155 polypropylene Polymers 0.000 claims description 2
- PPBRXRYQALVLMV-UHFFFAOYSA-N Styrene Chemical compound C=CC1=CC=CC=C1 PPBRXRYQALVLMV-UHFFFAOYSA-N 0.000 claims 2
- 239000004698 Polyethylene Substances 0.000 claims 1
- IRPDISVJRAYFBI-UHFFFAOYSA-N nitric acid;potassium Chemical compound [K].O[N+]([O-])=O IRPDISVJRAYFBI-UHFFFAOYSA-N 0.000 claims 1
- 229920000573 polyethylene Polymers 0.000 claims 1
- 230000006641 stabilisation Effects 0.000 claims 1
- 238000011105 stabilization Methods 0.000 claims 1
- 238000005265 energy consumption Methods 0.000 abstract description 2
- 230000001681 protective effect Effects 0.000 abstract 1
- 238000005086 pumping Methods 0.000 abstract 1
- 229910001385 heavy metal Inorganic materials 0.000 description 14
- FGIUAXJPYTZDNR-UHFFFAOYSA-N potassium nitrate Chemical compound [K+].[O-][N+]([O-])=O FGIUAXJPYTZDNR-UHFFFAOYSA-N 0.000 description 8
- 230000008569 process Effects 0.000 description 7
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 description 6
- 230000003647 oxidation Effects 0.000 description 6
- 238000007254 oxidation reaction Methods 0.000 description 6
- 239000000203 mixture Substances 0.000 description 5
- 238000012851 eutrophication Methods 0.000 description 4
- 230000012010 growth Effects 0.000 description 4
- 239000004323 potassium nitrate Substances 0.000 description 4
- 235000010333 potassium nitrate Nutrition 0.000 description 4
- 241000108664 Nitrobacteria Species 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 229910052500 inorganic mineral Inorganic materials 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 3
- 235000010755 mineral Nutrition 0.000 description 3
- 239000011707 mineral Substances 0.000 description 3
- 238000002360 preparation method Methods 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000006228 supernatant Substances 0.000 description 3
- 229910052785 arsenic Inorganic materials 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000005189 flocculation Methods 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- FBAFATDZDUQKNH-UHFFFAOYSA-M iron chloride Chemical compound [Cl-].[Fe] FBAFATDZDUQKNH-UHFFFAOYSA-M 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N iron oxide Inorganic materials [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 239000010410 layer Substances 0.000 description 2
- NDLPOXTZKUMGOV-UHFFFAOYSA-N oxo(oxoferriooxy)iron hydrate Chemical compound O.O=[Fe]O[Fe]=O NDLPOXTZKUMGOV-UHFFFAOYSA-N 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- FRXSZNDVFUDTIR-UHFFFAOYSA-N 6-methoxy-1,2,3,4-tetrahydroquinoline Chemical compound N1CCCC2=CC(OC)=CC=C21 FRXSZNDVFUDTIR-UHFFFAOYSA-N 0.000 description 1
- 239000002028 Biomass Substances 0.000 description 1
- 206010057249 Phagocytosis Diseases 0.000 description 1
- 239000004793 Polystyrene Substances 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 238000012271 agricultural production Methods 0.000 description 1
- 150000001336 alkenes Chemical class 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 238000011953 bioanalysis Methods 0.000 description 1
- 230000000740 bleeding effect Effects 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000001727 in vivo Methods 0.000 description 1
- 230000006698 induction Effects 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 229910052745 lead Inorganic materials 0.000 description 1
- 239000002905 metal composite material Substances 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 230000005012 migration Effects 0.000 description 1
- 238000013508 migration Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 229920000620 organic polymer Polymers 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 230000008782 phagocytosis Effects 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229920002223 polystyrene Polymers 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 238000012549 training Methods 0.000 description 1
- 230000032258 transport Effects 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
- C02F3/2806—Anaerobic processes using solid supports for microorganisms
-
- H—ELECTRICITY
- H02—GENERATION; CONVERSION OR DISTRIBUTION OF ELECTRIC POWER
- H02J—CIRCUIT ARRANGEMENTS OR SYSTEMS FOR SUPPLYING OR DISTRIBUTING ELECTRIC POWER; SYSTEMS FOR STORING ELECTRIC ENERGY
- H02J7/00—Circuit arrangements for charging or depolarising batteries or for supplying loads from batteries
- H02J7/34—Parallel operation in networks using both storage and other dc sources, e.g. providing buffering
- H02J7/35—Parallel operation in networks using both storage and other dc sources, e.g. providing buffering with light sensitive cells
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- 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
- C02F2103/007—Contaminated open waterways, rivers, lakes or ponds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/009—Apparatus with independent power supply, e.g. solar cells, windpower, fuel cells
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E10/00—Energy generation through renewable energy sources
- Y02E10/50—Photovoltaic [PV] energy
- Y02E10/56—Power conversion systems, e.g. maximum power point trackers
Abstract
The invention discloses a kind of solar anaerobic reactor assembly applied in natural water and its application method, the device include anaerobic reactor, into water conduit tube, go out water conduit tube, interior return duct, pump, accumulator, photoelectric controller, inverter and generator；Anaerobic reactor includes reaction kettle, electric heating assembly and solar photovoltaic assembly, reaction kettle is divided into reaction kettle top, reaction kettle middle part and reaction kettle lower part, reaction kettle top is connected with going out water conduit tube, in in the middle part of reaction kettle filler material is activated full of denitrifying bacteria, water distributor in reaction kettle lower part is connected by pumping with into water conduit tube, is intake, is gone out between water conduit tube equipped with interior return duct；Electric heating assembly is set in anaerobic reactor side wall；Solar photovoltaic assembly, accumulator, photoelectric controller, inverter, the control system of generator are sequentially connected, and generator is connected with electric heating assembly and pump.The present invention is without energy consumption, pollution-free, versatility is good, environmentally protective, and does not destroy the landscape function that some water bodys have.
Description
Technical field
The present invention relates to anaerobic reactor devices, and in particular to removes eutrophic water using water body original inhabitants denitrifying bacteria
A kind of solar anaerobic reactor assembly applied in natural water and its application method of heavy metal and nitrate nitrogen in body.
Background technology
Eutrophication of natural water and heavy metal pollution are always current most common combined pollution.Eutrophication is current
Important behaviour in conventional pollution, as the mankind increasingly increase environmental resource utilization activity, particularly industrial and agricultural production
Extensive development, largely the sewage containing compound fertilizer be discharged into neighbouring natural water body, add the battalion of these water bodys
Substance load is supported, essential problem is the multifarious destruction of aqueous bio, and the system that thereby results in is lost self―sustaining, self adjusted
The ability of section and system balancing unstability accelerate the speed of body eutrophication.And in the discharge process of sewage, pollutant
Heavy metal retaining in water body water body is also increasing, and heavy metal retaining in water body accumulates and the features such as migration increases
The difficulty that heavy metal in water has been added to purify.Simultaneously as heavy metal has, source is wide, the residence time is long, has accumulation property, can not drop
Solution can not only endanger Fishery Water Environment and aquatile, also endanger human health along the features such as food chain transport.Therefore compel
Being essential will be administered and be repaired to the water body water body of nitrate nitrogen and heavy-metal composite pollution.
The existing administering method for polluted water body can be divided into Physical, chemical method, bioanalysis, restoration of the ecosystem
Four major classes, and many method for treating water technological processes are very ripe, but deposited for the improvement of the open water body such as water body, river
In significant limitation.Therefore, from financial cost and recycling angularly, economical and efficient, energy-saving and environment-friendly water are explored
Weight metal purification method and device is the difficult point that current heavy metal pollution of water body is administered.
The content of the invention
Present invention aims to overcome that the deficiencies in the prior art, provide a kind of solar anaerobic applied in natural water
Reactor assembly and its application method.
A kind of solar anaerobic reactor assembly applied in natural water, including anaerobic reactor, into water conduit tube, go out
Water conduit tube, interior return duct, pump, accumulator, photoelectric controller, inverter and generator；The anaerobic reactor includes reaction
Kettle, electric heating assembly and solar photovoltaic assembly, anaerobic reactor top are provided with one-way exhaust valve；The reaction kettle is vertical
The closed tank body set, reaction kettle are divided into reaction kettle top, reaction kettle middle part and reaction kettle lower part, three are set in reaction kettle top
Phase separator, reaction kettle top are provided with water outlet, and the water outlet is connected with the water conduit tube that goes out；The reaction kettle
In middle part be equipped with spacer-frame, spacer-frame full of denitrifying bacteria activate filler material, the denitrifying bacteria activate filler material with
Inorganic carrying body, inorganic flocculate, inorganic metal salt, activated carbon are prepared for raw material, and the mass ratio of four kinds of raw materials is followed successively by
(1~8)：(0~0.5)：(0~0.5)：(2~4), wherein the quality of inorganic flocculate and inorganic metal salt ratio value range is
More than 0 and less than or equal to 0.5, four kinds of raw materials, which are sufficiently mixed, to be dispersed in 60~80 DEG C of water, is added in after cooling anti-
Nitrobacteria activator, the organic polymer being then dissolved in the water in the case where being sufficiently stirred with the speed instillation of 3~4ml/min gather
Object is closed, organic high molecular polymer is used to denitrifying bacteria activator being fixed on inorganic carrying body surface, after cooling precipitates, under
Portion's deposit is the denitrifying bacteria activation filler material, and the inorganic carrying body is in silica gel, montmorillonite or diatomite
One kind, the inorganic flocculate is aluminium polychloride (PAC), polyaluminium sulfate (PAS), bodied ferric sulfate (PFS) or poly-
One kind in iron chloride (PFC) is closed, the inorganic metal salt is sodium chloride, one kind in potassium chloride, the denitrifying bacteria
Activator ingredient is frerrous chloride, sodium acetate, peptone, yeast extract, glucose, sodium chloride, agar, potassium nitrate, matter during addition
Amount ratio is followed successively by (1~1.5)：(2~2.5)：(15~16)：(3~3.5)：(1~1.5)：(6~6.5)：(12~13)：(2~
2.5)；Water distributor is provided in reaction kettle lower part, water distributor is connected by the pump with described into water conduit tube, it is described into
Water conduit tube and go out between water conduit tube to be provided with the interior return duct；Hollow folder is provided in the anaerobic reactor side wall
Layer, the electric heating assembly are arranged in hollow interlayer and are evenly distributed on anaerobic reactor side wall；The solar energy
Volt component is connected with the accumulator, and accumulator is connected with the photoelectric controller, and photoelectric controller is connected with inverter,
Inverter is connected with the control system of the generator, and generator is connected with electric heating assembly and pump.
Moreover, system must be cooled to 30~40 DEG C when adding in the denitrifying bacteria activator, and control itself and nothing
The ratio of machine carrying body is (0.3~8)：1, preferably (3~5)：1；The organic high molecular polymer is polyvinyl alcohol, poly- second
One kind in alkene, polypropylene, polystyrene or cellulose, the organic high molecular polymer are dispersed in 95~97 DEG C
In water, the final mass ratio of the organic high molecular polymer and inorganic carrying body is (0.5~0.6)：(7~8).
Moreover, described going out on water conduit tube is provided with out water regulating valve, go out the other end connection staying water of water conduit tube
Water outlet；It is described into inlet regulating valve is provided on water conduit tube, the other end into water conduit tube connects staying water water inlet；
Return valve is provided on the interior return duct.
Moreover, the reaction kettle top and the outer surface of reaction kettle lower part are arc-shaped, reaction kettle top and reaction kettle
High 0.2~the 0.4m in lower part, the high 0.2~0.4m in bottom；It is cylinder, a diameter of 0.5~1m, high 1~3m in the middle part of reaction kettle.
Moreover, the denitrifying bacteria activation filler material is filled in using the method for lattice filling in reaction kettle middle part,
It is close fill out that total height is reaction kettle total height 75%~90%, the distance at the top of denitrifying bacteria Activation filling and reaction kettle is anti-
Answer the 10%~25% of kettle total height, the disposable 1000~4000mg/L of dosage of technique initial period.
Moreover, the electric heating assembly is made of the heating wire of n groups parallel connection, 10≤n≤40, heating wire is in vertical direction
It is upper S-type, and heating wire is integrally along reaction kettle axial rings around annular in shape.
A kind of application method for the solar anaerobic reactor assembly applied in natural water, comprises the following steps：
Step 1, a kind of solar anaerobic reactor assembly applied in natural water is placed in accessing pending water
Body bank measures the quantity of indigenous denitrifying bacteria in the water body water body using the method for quantitative fluorescent PCR；
Step 2, the equipment is run, inlet regulating valve and return valve is opened, closes out water regulating valve, utilize solar energy
The energy hole pump that photovoltaic module generates is introduced from water body intakes, and realizes the self-loopa of technique initial period internal system, herein
Stage denitrifying bacteria microorganism carries out biofilm culture, and it is thin that denitrification after adding in water body is measured by the method for quantitative fluorescent PCR
Denitrifying bacteria quantity in bacterium activation filler material realizes that the multiple that the quantity of indigenous denitrifying bacteria increases is more than or equal to 10；
Step 3, inlet regulating valve and return valve is kept to open, then opens out water regulating valve, when controlling normal operation
Flow of inlet water, control hydraulic detention time, by adjust inlet regulating valve, go out water regulating valve and return valve control Inlet and outlet water
Ratio and nitrate recirculation ratio；
Step 4, the water outlet in anaerobic reactor device is again flowed by self gravitation in staying water；
In step 2 and step 3, solar photovoltaic assembly, which converts solar energy into electrical energy, is stored in solar storage battery
It is interior, then direct current energy signal is converted by photoelectric control prop, DC signal enters inverter and is being converted into AC load
Ac electric apparatus is supplied, then electric energy is provided for the electric heating assembly of solar photovoltaic assembly lower floor by generator control system, electricity
Heating component converts electrical energy into thermal energy, and electric heating assembly is all covered in tank surface, effectively accomplished in anaerobic reactor
Heated liquid is uniform；Meanwhile generator control system provides electric energy for pump, during realizing the self-loopa of the device and normal operation
Stable state.
Moreover, in above-mentioned application method, the technique initial period internal system self-loopa time is 24~26h,
0.1~0.9m of flow of inlet water during normal operation3/ h, described controls hydraulic detention time as 6~10h, the nitrate recirculation ratio
Example is 400%~500%.
Beneficial effects of the present invention：
(1) a kind of solar anaerobic reactor assembly applied in natural water is net using the ecology of eutrophication water
Change method by activating the denitrifying bacteria in water body native country, makes denitrifying bacteria quantity rise in value in geometric progression, and uses water body
Itself replaces traditional limited bioreactor, releases denitrifying bacteria growing space significantly, gives full play to denitrifying bacteria
The powerful capacity of decomposition generated during amount reproduction to nitrate nitrogen improves the effective biomass and function of denitrifying bacteria
Property, restructuring is improved and optimizes Water microbial ecology system, and then strengthens microorganism central hub effect of establishing, and promotes water body
Recover capacity of self-regulation, so as to which efficiently N, P of removal induction algal blooms etc. are contaminants associated, effectively reduce in water body
Suspended alga, suspended particulate content, reduce turbidity, increase transparency, it is horizontal to promote Dissolved Oxygen in Water, fundamentally improves water
The material balance state of matter and water ecosystem is finally reached and keeps the restoration of the ecosystem purpose of the self-purification of water.
(2) present invention process is simple, and floor space is small, and operational management is convenient, invests, condition of compatibility model low with operating cost
It encloses extensively, it can the extensive use in various natural water body restorations of the ecosystem.
(3) a kind of solar anaerobic reactor assembly applied in natural water involved in this technology, outermost layer are
Solar photovoltaic assembly, is mainly used for converting solar energy into electrical energy and is stored in solar storage battery, then passes through photoelectric control branch
Device is converted into direct current energy signal, and DC signal can directly be used in DC electric apparatus, can also be converted into inverter
AC load removes supply ac electric apparatus, then is carried by generator control system for the electric heating assembly of solar photovoltaic assembly lower floor
For electric energy, electric heating assembly converts electrical energy into thermal energy, and electric heating assembly is all covered in tank surface, can effectively accomplished
Heated liquid is uniform in anaerobic reactor, and suitable temperature is provided for microorganism, convenient for the growth of microorganism, the activity of microorganism
It is protected with flora number, the in vivo biological activated sludge of tank is with regard to that can have the work that preferable phagocytosis Organic substance in water is decomposed
With, stable anaerobism purification is carried out to water body, meanwhile, generator control system provides electric energy for pump, with realize the device oneself
Stable state when Xun Huan and normal operation.For the heat preserving method of now existing other forms, the photovoltaic installed
Component and electric heating assembly have apparent advantage, without energy consumption, pollution-free, good without operating cost, versatility, not only green ring
It protects, and does not destroy the landscape function that some water bodys have.Therefore, the device use condition is very wide, throughout the year except cold zone not
Seeing the place of sunlight cannot use, and secondary pollution is not caused after non-maintaining use, be real clean energy resource, and energy quality is high,
The time for obtaining the energy is short.System one-time investment can keep continuously power supply 20 years.
(4) during denitrifying bacteria multiplication, Fe2+While playing the role of being obviously promoted in the process, aoxidized
The ferric oxide of generation has heavy metal that can largely in adsorbed water body, effectively removes the heavy metal in water body.
Description of the drawings
Fig. 1 is the schematic diagram of the present invention.
Wherein：1 is anaerobic reactor, and 2 be water outlet, and 3 be water conduit tube, and 4 be reaction kettle top, and 5 be reaction kettle middle part,
6 be reaction kettle lower part, and 7 be water regulating valve, and 8 be staying water, and 8-1 is staying water water outlet, and 8-2 is accessing pending water
Body water inlet, 9 be inlet regulating valve, and 10 be into water conduit tube, and 11 be return valve, and 12 be interior return duct, and 13 be pump, and 14 be to fill out
Lattice are filled, 15 be water distributor, and 16 be ferric oxide and heavy metal outlet, and 17 be accumulator, and 18 be photoelectric controller, and 19 are
Generator, 20 be inverter, and 21 be reaction kettle, and 22 be solar photovoltaic assembly, and 23 be hollow interlayer, and 24 be reaction kettle, and 25 are
Three phase separator, 26 be one-way exhaust mouth.
Specific embodiment
The present invention is further illustrated with reference to the accompanying drawings and examples.
A kind of solar anaerobic reactor assembly applied in natural water, including anaerobic reactor 1, into water conduit tube
10th, water conduit tube 3, interior return duct 12, pump 13, accumulator 17, photoelectric controller 18, inverter 20 and generator 19 are gone out；Described
Anaerobic reactor includes reaction kettle 24, electric heating assembly 22 and solar photovoltaic assembly 21, and list is provided at the top of anaerobic reactor
To air bleeding valve 26；The closed tank body that the reaction kettle is vertically arranged, reaction kettle are divided into reaction kettle top 4,5 and of reaction kettle middle part
Reaction kettle lower part 6 sets three phase separator 25 in reaction kettle top, and reaction kettle top is provided with water outlet 2, the water outlet
It is connected with the water conduit tube 3 that goes out, interior in the middle part of the reaction kettle to be equipped with spacer-frame 14, spacer-frame is activated full of denitrifying bacteria
Filler material is provided with water distributor 15 in reaction kettle lower part, and water distributor is connected by the pump 13 with described into water conduit tube 10,
It is described into water conduit tube and to go out between water conduit tube to be provided with the interior return duct 12；It is set in the anaerobic reactor side wall
There is hollow interlayer 23, the electric heating assembly is arranged in hollow interlayer 23 and is evenly distributed on anaerobic reactor side wall；
The solar photovoltaic assembly is connected with the accumulator 17, and accumulator is connected with the photoelectric controller 18, photoelectric control
Device processed is connected with inverter 20, and inverter is connected with the control system of the generator 19, generator and electric heating assembly and
Pump connection.
Moreover, described going out on water conduit tube is provided with out water regulating valve 7, go out the other end connection staying water of water conduit tube
Water outlet 8-1；It is described into being provided with inlet regulating valve 9 on water conduit tube, into water conduit tube the other end connect staying water into
Mouth of a river 8-2；Return valve 11 is provided on the interior return duct.
Moreover, the reaction kettle top and the outer surface of reaction kettle lower part are arc-shaped, reaction kettle top and reaction kettle
The high 0.2m in lower part, the high 0.2m in bottom；It is cylinder, a diameter of 0.8m, high 3m in the middle part of reaction kettle.
Moreover, the denitrifying bacteria activation filler material is filled in using the method for lattice filling in reaction kettle middle part,
It is close fill out that total height is reaction unit total height 85%, the distance at the top of denitrifying bacteria Activation filling and reaction kettle fills for reaction
Put the 15% of total height, the disposable dosage 3000mg/L of technique initial period.
Moreover, the electric heating assembly is made of 35 groups of heating wire in parallel, heating wire is S-type in the vertical direction,
And heating wire entirety is along reaction kettle axial rings around annular in shape.
The denitrifying bacteria prepared according to following preparation method activation filler material is filled in above-mentioned a kind of apply in nature
In solar anaerobic reactor assembly in water body：It is 3 by mass ratio：0.5：0.5：4 inorganic carrying body silica gel, inorganic flocculation
Object polymer alumina, inorganic metal salt sodium chloride, activated carbon are sufficiently mixed and are scattered in 70 DEG C of water, treat above-mentioned suspension
Be cooled to 40 DEG C, add in denitrifying bacteria activator (activator by frerrous chloride, sodium acetate, peptone, yeast extract, glucose,
Sodium chloride, agar, potassium nitrate composition, mass ratio is followed successively by 1 when each ingredient adds：2：15：3：1：6：12：2；It is anti-described in adding in
System must be cooled to 30 DEG C during nitrobacteria activator), the ratio for controlling itself and inorganic carrying body is 3, is then being sufficiently stirred
While organic high molecular polymer polyvinyl alcohol in 95 DEG C of water is dissolved in the instillation of the speed of 3ml/min, for fixed anti-
Nitrobacteria activator is final to realize that organic high molecular polymer and the mass ratio of inorganic carrying body are in inorganic carrying body surface
0.5：8, after liquid to be mixed is cooled to room temperature precipitation, abandoning supernatant, specific denitrifying bacteria made from the deposit of lower part lives
Change filler material；After filler material loads, which is placed in staying water bank, runs the device, opens water inlet
Regulating valve and return valve, close out water regulating valve, and water inlet (profit is introduced from staying water using the power that solar energy generates
The quantity that indigenous denitrifying bacteria in the water body water body is measured with the method for quantitative fluorescent PCR is 106-107Copies/L), realize
When the time is 24 small, biofilm training is carried out in this stage denitrifying bacteria microorganism for the self-loopa of technique initial period internal system
Support, control hydraulic detention time for 8 it is small when, by the method for quantitative fluorescent PCR, after obtaining addition accessing pending water precursor reactant for 24 hours
Denitrifying bacteria quantity in denitrifying bacteria activation filler material is about 107-108Copies/g (the numbers of i.e. indigenous denitrifying bacteria
Amount realizes 10 times of growths)；Finally, inlet regulating valve and return valve is kept to open, then opens out water regulating valve, control is normal
Flow of inlet water 0.9m during operation3/ h, control hydraulic detention time for 9 it is small when, by adjust inlet regulating valve, go out water regulating valve and
It is 400% that return valve, which controls Inlet and outlet water ratio and nitrate recirculation ratio example,.Denitrifying bacteria in this process constantly treat by removal
Handle the nitrate nitrogen in water body, and Oxidation of Fe2+Form Fe3+With amorphous Fe3+Based on mineral, without unit in thalline deposit
Into based on Fe, contain a small amount of heavy metal As5+, in Fe2+NO in the case of oxidation totally3 -Average removal rate up to 40~
The average removal rate of 60%, As are up to 40~70%.
The denitrifying bacteria prepared according to following preparation method activation filler material is filled in above-mentioned a kind of apply in nature
In solar anaerobic reactor assembly in water body：It is 4 by mass ratio：0.5：0.5：4 inorganic carrying body montmorillonite, inorganic wadding
Condensate poly-ferric chloride, inorganic metal salt sodium chloride, activated carbon are sufficiently mixed and are scattered in 70 DEG C of water, are treated above-mentioned suspended
Liquid is cooled to 40 DEG C, and adding in denitrifying bacteria activator, (activator is by frerrous chloride, sodium acetate, peptone, yeast extract, grape
Sugar, sodium chloride, agar, potassium nitrate composition, mass ratio is followed successively by 1.2 when each ingredient adds：2：16：3：1.5：6：13：2；It adds in
System must be cooled to 35 DEG C during described denitrifying bacteria activator), the ratio for controlling itself and inorganic carrying body is 4, Ran Hou
The organic high molecular polymer polyvinyl alcohol being dissolved in 95 DEG C of water is instilled with the speed of 3ml/min while being sufficiently stirred, is used
It is final to realize organic high molecular polymer and inorganic carrying body in fixed denitrifying bacteria activator in inorganic carrying body surface
Mass ratio is 0.6：7, after liquid to be mixed is cooled to room temperature precipitation, abandoning supernatant, the anti-nitre of specificity made from the deposit of lower part
Change bacterium activation filler material；After filler material loads, which is placed in staying water bank, runs the device,
Inlet regulating valve and return valve are opened, closes out water regulating valve, the power generated using solar energy is drawn from staying water
Enter that (quantity that indigenous denitrifying bacteria is measured in the water body water body using the method for quantitative fluorescent PCR is 10 into water5-
106Copies/L), the self-loopa of technique initial period internal system is realized, when the time is 24 small, in this stage denitrifying bacteria
Microorganism carry out biofilm culture, control hydraulic detention time be 8 it is small when, by the method for quantitative fluorescent PCR, obtain adding in and wait to locate
It is about 10 to manage the water body reaction denitrifying bacteria quantity that rear denitrifying bacteria is activated in filler material for 24 hours6-107Copies/g is (i.e. native
The quantity for writing denitrifying bacteria realizes 10 times of growths)；Finally, inlet regulating valve and return valve is kept to open, then is opened out
Water regulating valve, flow of inlet water 0.9m when controlling normal operation3/ h, control hydraulic detention time for 9 it is small when, pass through adjust water inlet adjust
Section valve goes out water regulating valve and return valve control Inlet and outlet water ratio and nitrate recirculation ratio example as 400%.Denitrifying bacteria is at this
Nitrate nitrogen constantly in removal staying water in the process, and Oxidation of Fe2+Form Fe3+With amorphous Fe3+Based on mineral, bacterium
Inorganic composition contains a small amount of heavy metal As based on Fe in body deposit5+, in Fe2+NO in the case of oxidation totally3 -Removal
Rate is up to the removal rate of 30~40%, As up to 30~40%.
The denitrifying bacteria prepared according to following preparation method activation filler material is filled in above-mentioned a kind of apply in nature
In solar anaerobic reactor assembly in water body：It is 3 by mass ratio：0.5：0.5：3 inorganic carrying body silica gel, inorganic flocculation
Object bodied ferric sulfate, inorganic metal salt potassium chloride, activated carbon are sufficiently mixed and are scattered in 80 DEG C of water, treat above-mentioned suspension
Be cooled to 40 DEG C, add in denitrifying bacteria activator (activator by frerrous chloride, sodium acetate, peptone, yeast extract, glucose,
Sodium chloride, agar, potassium nitrate composition, mass ratio is followed successively by 1.2 when each ingredient adds：2.5：16：3.5：1.5：6：13：2；It adds in
System must be cooled to 40 DEG C during described denitrifying bacteria activator), the ratio for controlling itself and inorganic carrying body is 1, Ran Hou
The organic high molecular polymer polyvinyl alcohol being dissolved in 95 DEG C of water is instilled with the speed of 3ml/min while being sufficiently stirred, is used
It is final to realize organic high molecular polymer and inorganic carrying body in fixed denitrifying bacteria activator in inorganic carrying body surface
Mass ratio is 0.5：8, after liquid to be mixed is cooled to room temperature precipitation, abandoning supernatant, the anti-nitre of specificity made from the deposit of lower part
Change bacterium activation filler material；After filler material loads, which is placed in staying water bank, runs the device,
Inlet regulating valve and return valve are opened, closes out water regulating valve, the power generated using solar energy is drawn from staying water
Enter that (quantity that indigenous denitrifying bacteria is measured in the water body water body using the method for quantitative fluorescent PCR is 10 into water6-
107Copies/L), the self-loopa of technique initial period internal system is realized, when the time is 24 small, in this stage denitrifying bacteria
Microorganism carry out biofilm culture, control hydraulic detention time be 8 it is small when, by the method for quantitative fluorescent PCR, obtain adding in and wait to locate
It is about 10 to manage the water body reaction denitrifying bacteria quantity that rear denitrifying bacteria is activated in filler material for 24 hours7-108Copies/g is (i.e. native
The quantity for writing denitrifying bacteria realizes 10 times of growths)；Finally, inlet regulating valve and return valve is kept to open, then is opened out
Water regulating valve, flow of inlet water 0.9m when controlling normal operation3/ h, control hydraulic detention time for 9 it is small when, pass through adjust water inlet adjust
Section valve goes out water regulating valve and return valve control Inlet and outlet water ratio and nitrate recirculation ratio example as 400%.Denitrifying bacteria is at this
Nitrate nitrogen constantly in removal staying water in the process, and Oxidation of Fe2+Form Fe3+With amorphous Fe3+Based on mineral, bacterium
Inorganic composition contains a small amount of heavy metal Pb based on Fe in body deposit5+, in Fe2+NO in the case of oxidation totally3 -Removal
Rate is up to the removal rate of 50~60%, Pb up to 40~50%.
It is adjusted using technical solution disclosed in present invention and prepares different filler materials, when carrying out sewage disposal
Show the property basically identical with embodiment.Illustrative description is done to the present invention above, it should which explanation is not taking off
In the case of core from the present invention, any simple deformation, modification or other skilled in the art can not spend wound
The equivalent substitution of the property made work each falls within protection scope of the present invention.
Claims (8)
1. a kind of solar anaerobic reactor assembly applied in natural water, it is characterised in that：Including anaerobic reactor, into
Water conduit tube goes out water conduit tube, interior return duct, pump, accumulator, photoelectric controller, inverter and generator；The anaerobic reactor
Including reaction kettle, electric heating assembly and solar photovoltaic assembly, one-way exhaust valve is provided at the top of anaerobic reactor；The reaction
The closed tank body that kettle is vertically arranged, reaction kettle are divided into reaction kettle top, reaction kettle middle part and reaction kettle lower part, reaction kettle top
Interior setting three phase separator, reaction kettle top are provided with water outlet, and the water outlet is connected with the water conduit tube that goes out；It is described
Reaction kettle in the middle part of in be equipped with spacer-frame, spacer-frame full of denitrifying bacteria activate filler material, the denitrifying bacteria activation
Filler material is prepared using inorganic carrying body, inorganic flocculate, inorganic metal salt, activated carbon as raw material, the quality of four kinds of raw materials
Than being followed successively by (1~8)：(0~0.5)：(0~0.5)：(2~4), wherein the mass ratio of inorganic flocculate and inorganic metal salt takes
It is more than 0 and less than or equal to 0.5 to be worth scope, and four kinds of raw materials, which are sufficiently mixed, to be dispersed in 60~80 DEG C of water, cooling
Denitrifying bacteria activator is added in afterwards, is then dissolved in the water in the case where being sufficiently stirred with the speed instillation of 3~4ml/min organic
High molecular polymer, organic high molecular polymer are used to denitrifying bacteria activator being fixed on inorganic carrying body surface, cool down
After precipitation, lower part deposit is denitrifying bacteria activation filler material, the inorganic carrying body is silica gel, montmorillonite or
One kind in diatomite, the inorganic flocculate is aluminium polychloride (PAC), polyaluminium sulfate (PAS), bodied ferric sulfate
(PFS) or one kind in poly-ferric chloride (PFC), the inorganic metal salt be sodium chloride, one kind in potassium chloride, it is described
Denitrifying bacteria activator ingredient is frerrous chloride, sodium acetate, peptone, yeast extract, glucose, sodium chloride, agar, nitric acid
Potassium, mass ratio is followed successively by (1~1.5) during addition：(2~2.5)：(15~16)：(3~3.5)：(1~1.5)：(6~6.5)：
(12~13)：(2~2.5)；Be provided with water distributor in reaction kettle lower part, water distributor by the pump with it is described into water conduit tube
Connection, it is described that the interior return duct is provided with into water conduit tube and going out between water conduit tube；In the anaerobic reactor side wall
Hollow interlayer is provided with, the electric heating assembly is arranged in hollow interlayer and is evenly distributed on anaerobic reactor side wall；
The solar photovoltaic assembly is connected with the accumulator, and accumulator is connected with the photoelectric controller, photoelectric controller
It is connected with inverter, inverter is connected with the control system of the generator, and generator is connected with electric heating assembly and pump.
2. a kind of solar anaerobic reactor assembly applied in natural water according to claim 1, feature exist
In：System must be cooled to 30~40 DEG C when adding in the denitrifying bacteria activator, and control itself and inorganic carrying body
Ratio is (0.3~8)：1, preferably (3~5)：1；The organic high molecular polymer is polyvinyl alcohol, polyethylene, polypropylene, poly-
One kind in styrene or cellulose, the organic high molecular polymer is dispersed in 95~97 DEG C of water, described
Organic high molecular polymer and the final mass ratio of inorganic carrying body are (0.5~0.6)：(7~8).
3. a kind of solar anaerobic reactor assembly applied in natural water according to claim 1, feature exist
In：Described going out on water conduit tube is provided with out water regulating valve, goes out the other end connection staying water water outlet of water conduit tube；It is described
Into inlet regulating valve is provided on water conduit tube, the other end into water conduit tube connects staying water water inlet；Described interior time
Return valve is provided in flow tube.
4. a kind of solar anaerobic reactor assembly applied in natural water according to claim 1, feature exist
In：The reaction kettle top and the outer surface of reaction kettle lower part be it is arc-shaped, reaction kettle top and reaction kettle lower part it is high by 0.2~
0.4m, the high 0.2~0.4m in bottom；It is cylinder, a diameter of 0.5~1m, high 1~3m in the middle part of reaction kettle.
5. a kind of solar anaerobic reactor assembly applied in natural water according to claim 1, feature exist
In：The denitrifying bacteria activation filler material is filled in using the method for lattice filling in reaction kettle middle part, close to fill out total height
For the 75%~90% of reaction kettle total height, denitrifying bacteria Activation filling is reaction kettle total height with the distance at the top of reaction kettle
10%~25%, the disposable 1000~4000mg/L of dosage of technique initial period.
6. a kind of solar anaerobic reactor assembly applied in natural water according to claim 1, feature exist
In：The electric heating assembly is made of the heating wire of n groups parallel connection, and 10≤n≤40, heating wire is S-type in the vertical direction, and
And heating wire is integrally along reaction kettle axial rings around annular in shape.
7. a kind of user of solar anaerobic reactor assembly applied in natural water according to claim 1
Method comprises the following steps：
Step 1, staying water bank is placed in by the anaerobic reactor device of Driven by Solar Energy by described, utilizes fluorescent quantitation
The method of PCR measures the quantity of indigenous denitrifying bacteria in the water body water body；
Step 2, the equipment is run, inlet regulating valve and return valve is opened, closes out water regulating valve, utilize photovoltaic
The energy hole pump that component generates is introduced from water body intakes, and the self-loopa of technique initial period internal system is realized, in this stage
Denitrifying bacteria microorganism carries out biofilm culture, and denitrifying bacteria after adding in water body is measured by the method for quantitative fluorescent PCR and is lived
Change the denitrifying bacteria quantity in filler material, realize that the multiple that the quantity of indigenous denitrifying bacteria increases is more than or equal to 10；
Step 3, inlet regulating valve and return valve is kept to open, then opens out water regulating valve, is intake when controlling normal operation
Flow, control hydraulic detention time, by adjust inlet regulating valve, go out water regulating valve and return valve control Inlet and outlet water ratio
And nitrate recirculation ratio；
Step 4, the water outlet in anaerobic reactor device is again flowed by self gravitation in staying water；
In step 2 and step 3, solar photovoltaic assembly, which converts solar energy into electrical energy, to be stored in solar storage battery, then
Direct current energy signal is converted by photoelectric control prop, DC signal enters inverter and supply gone to hand over being converted into AC load
Galvanic electricity device, then by generator control system electric energy, electrical heating group are provided for the electric heating assembly of solar photovoltaic assembly lower floor
Part converts electrical energy into thermal energy, and electric heating assembly is all covered in tank surface, effectively accomplish in anaerobic reactor liquid by
It is hot uniform；Meanwhile generator control system provides electric energy for pump, to realize the stabilization when self-loopa of the device and normal operation
State.
8. a kind of user of solar anaerobic reactor assembly applied in natural water according to claim 7
Method, it is characterised in that：The technique initial period internal system self-loopa time is 24~26h, feed water flow during normal operation
Measure 0.1~0.9m3/ h, described controls hydraulic detention time as 6~10h, and the nitrate recirculation ratio example is 400%~500%.
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Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101844830A (en) * | 2009-03-25 | 2010-09-29 | 株式会社日立工业设备技术 | Method of wastewater treatment |
| CN102701442A (en) * | 2012-05-22 | 2012-10-03 | 青岛理工大学 | Quick start method of source water biological denitrification system |
| CN204848436U (en) * | 2015-08-12 | 2015-12-09 | 甘肃新天亿环保工程有限公司 | Solar energy anaerobic reactor device |
| CN105712497A (en) * | 2016-01-18 | 2016-06-29 | 同济大学 | Microbial activation method and system for eutrophicated water body ecological restoration |
| CN105948241A (en) * | 2016-06-03 | 2016-09-21 | 湖南恒凯环保科技投资有限公司 | Packed EGSB reactor |
-
2016
- 2016-11-15 CN CN201611020549.2A patent/CN108069510A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101844830A (en) * | 2009-03-25 | 2010-09-29 | 株式会社日立工业设备技术 | Method of wastewater treatment |
| CN102701442A (en) * | 2012-05-22 | 2012-10-03 | 青岛理工大学 | Quick start method of source water biological denitrification system |
| CN204848436U (en) * | 2015-08-12 | 2015-12-09 | 甘肃新天亿环保工程有限公司 | Solar energy anaerobic reactor device |
| CN105712497A (en) * | 2016-01-18 | 2016-06-29 | 同济大学 | Microbial activation method and system for eutrophicated water body ecological restoration |
| CN105948241A (en) * | 2016-06-03 | 2016-09-21 | 湖南恒凯环保科技投资有限公司 | Packed EGSB reactor |
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Application publication date: 20180525 |