CN102267748B - Combined device and method for repairing eutrophic water - Google Patents

Combined device and method for repairing eutrophic water Download PDF

Info

Publication number
CN102267748B
CN102267748B CN201110205094.2A CN201110205094A CN102267748B CN 102267748 B CN102267748 B CN 102267748B CN 201110205094 A CN201110205094 A CN 201110205094A CN 102267748 B CN102267748 B CN 102267748B
Authority
CN
China
Prior art keywords
water
water body
oxygen
fine molecular
permanent magnet
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201110205094.2A
Other languages
Chinese (zh)
Other versions
CN102267748A (en
Inventor
扈乃维
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing Dayu Huimin Environmental Technology Co ltd
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to CN201110205094.2A priority Critical patent/CN102267748B/en
Publication of CN102267748A publication Critical patent/CN102267748A/en
Application granted granted Critical
Publication of CN102267748B publication Critical patent/CN102267748B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention provides a combined device comprising a magnetizing device and a method for repairing eutrophic water, and belongs to the technical field of treatment of water, waste water or sewage. According to the method, a new materialized or biochemical dynamic balanced reaction system is established on the basis of ecological balance. According to the method, the oxygen content of the water is increased, and the biochemical reaction of microbes is complete; oxygen is dissolved in the water in a super-saturated mode, so that a large amount of aerobic microbes are propagated, decomposition of organic substances in the water is accelerated, and the nutrition source of algae is reduced. The combined device comprises a water pump, a fine molecular device, an oxygen generating device and the magnetizing device. The method comprises the following steps of: making the eutrophic water flow through the fine molecular super-saturated oxygen dissolving device through the water pump, and magnetizing the small molecular eutrophic water flow after fine molecular super-saturated oxygen dissolution through the super-strong magnetizing device. The method is simple in process and low in cost, the self-purifying function of the water is recovered, the effect is lasting, and a brand-new treatment thought is provided for solving eutrophication of the water of a lake.

Description

A kind of combination unit and method of repairing eutrophication water
Technical field
The invention belongs to the processing technology field of water, waste water or sewage, specifically relate to a kind of combination unit and method of repairing eutrophication water.
Background technology
Body eutrophication refers to that the plant nutrient such as nitrogen, phosphorus enters the water body of the relative closures such as lake, river, bay, sluggish flow in a large number, cause the amount reproduction of algae and other waterplant, cause water transparency and dissolved oxygen to decline, water quality deterioration, other hydrobiont mortality, water ecosystem and function of water body are hindered and are destroyed.Body eutrophication is a kind of water body aging phenomenon.Owing to artificially and naturally destroying, excessive development and utilization, in many lakes and river, vigorous water has accelerated to eutrophic water fundamental change originally.
Mainly repair the ecosystem by controlling endogenous and exogenous nutrition material at present, in prior art, have about the patent of river, water body in lake restoration of the ecosystem aspect:
Publication number is the patent of invention that CN101607762A, denomination of invention are " ecological restoring method of river water body ", a kind of bio-diversity technical scheme of river water of recovering is disclosed, this technical scheme, for to throw in composite fungus agent, hydrocoles and/or planting aquatic plants in water body, makes the contamination index of water body reach appointment requirement.This method is by the step of duplicate detection River Water Pollution index-input composite fungus agent, reaches final requirement, and cost is higher.
Application number is the application for a patent for invention that CN201010596971.9, denomination of invention are " a kind of lake eutrophication remediation method ", disclose a kind of technical scheme of repairing lake eutrophication, the step that technical scheme comprises is: (1) buriedly sets gradually microorganism and repairs tank, absorption tank and cooling trough with half on loke shore; (2) microorganism repairing phase; (3) absorption phase; (4) cooling stages; (5) the restoration of the ecosystem stage in water.This patent application and foregoing invention patent starting point are biological restoration angle, and technical process is longer, and needs professional to operate, and has increased cost of sewage disposal.
And for example application number is the application for a patent for invention that CN200910057635.4, denomination of invention are " method of removing water eutrophication ", technical scheme is: hydrobiological structure of community in investigation water body, according to this investigation result, find out missing link or chain rupture link in food chain; In water body, put predacious fish in a suitable place to breed, take medicine mode or artificial fishing style, remove raw fish and herbivorous fishes in water body, adjust water body Fish Community Structures; The bottom of 0~1.5m depth of water kind planting submerged plant, floatingleaved plant and emergent; In water body, put filter-feeding fish, filter-feeding shellfish, chip feeding habits zoobenthos and herbivorous fishes in a suitable place to breed.This patent is also that treatment step is loaded down with trivial details from biological angle, has increased operation easier.
Prior art can obtain certain repairing effect as early as possible for the body eutrophication in river, lake, but because original ecosystem is destroyed, a little less than water body self-purification ability, the water body system to external world impact of environment lacks buffered ability, therefore the treatment effect of water body is difficult to maintain, and eutrophication pollution easily occurs again.And prior art is mainly from biological restoration angle, and the amount reproduction of algae is a kind of bad phenomenon that eutrophication is brought, only removing algae is not the method for effecting a permanent cure, and thoroughly deal with problems and also will consider from the angle of the eubiosis.
Present stage, main task was to inject vigour into eutrophication water or old and feeble water body, strengthened water body immunizing power, improved the detersive power of water body self, made water body become healthy, vital water.
Summary of the invention
The object of the invention is to provide a kind of combination unit and method of the reparation eutrophication water that comprises magnetizing assembly, mainly solve lake and river water eutrophication problem, the present invention is from the angle of the eubiosis, not only solve prolific algae, also improve water body self-purification ability, inject vigour into eutrophication water or old and feeble water body, strengthen water body immunizing power, permanently effective solution body eutrophication problem.The present invention has overcome the difficult points such as in traditional method, water body oxygen level is low, microbial biochemical reaction is incomplete, not only can be by super-saturated oxygen soluble in water, and can make aerobic microbiological amount reproduction, thus accelerate organic decomposition in water, reduce the nutrition source of algae.
For achieving the above object, the technical scheme that the present invention takes is:
A kind of water magnetizing device, described magnetizing assembly comprises magnetization passage and flange, described flange is positioned at the two ends of described magnetization passage; Its improvements are that described magnetization passage comprises inner ring and the outer wall of being made up of non-magnet_conductible material, and the excircle of described inner ring is provided with permanent magnet, and the inner periphery of described outer wall is provided with magnetic shielding material.
Another optimal technical scheme of the present invention is: the same axis of described inner ring and outer wall, being shaped as of described permanent magnet is fan-shaped.
Another optimal technical scheme of the present invention is: described permanent magnet and the laminating of described inner ring, leave space between described permanent magnet and described magnetic shielding material.
An optimal technical scheme more of the present invention is: described permanent magnet and described magnetic shielding material are sealed in the cavity inside that described inner ring, outer wall and flange form.
An optimal technical scheme more of the present invention is: the magnetic induction density B value of described magnetization channel interior is greater than 7 × 10 3gs.
An optimal technical scheme more of the present invention is: a kind of combination unit of the reparation eutrophication water that comprises magnetizing assembly, described combination unit comprises water pump, magnetizing assembly, fine molecular device and oxygenerator.
An optimal technical scheme more of the present invention is: described water pump, described magnetizing assembly and described oxygenerator are connected with described fine molecular device respectively.
An optimal technical scheme more of the present invention is: a kind of method of utilizing combination unit to repair eutrophication water, its improvements are that described method comprises the steps:
Water body is carried out to fine molecular over-saturation dissolved oxygen;
To in step 1 after fine molecular over-saturation dissolved oxygen water body magnetize.
Owing to having adopted technique scheme, compared with prior art, beneficial effect of the present invention comprises:
1) whole process management is concentrated, simple to operate, easy to maintenance, safe and reliable to operation
2) only need the power of current through equipment, without its other energy consumptions
3) equipment volume is little, lightweight
4) pollution-free, long service life
5) adapt to various conditions and environment
Accompanying drawing explanation
Below in conjunction with accompanying drawing, the present invention is further described.
Fig. 1 is magnetizing assembly overall schematic;
Fig. 2 is magnetizing assembly A-A schematic cross-section;
Fig. 3 is combination unit overall schematic;
1-magnetizes passage, 2-flange, 3-permanent magnet, 4-inner ring, 5-outer wall, 6-shielding material, 7-water pump, 8-magnetizing assembly, 9-fine molecular device, 10-oxygenerator, water body after 11-purifies, water body before 12-purifies.
Embodiment
Below in conjunction with example, the present invention will be described in detail.
The present invention is take the principle of material and energy balance as theoretical basis, take the many principle comprehensive coordinations of gas, liquid, solid " tri-state separation " materialization, biochemical reaction as mechanism, to recover and to bring into play water body self purification function as means, take the water ecological setting of creating a natural circulation as object, system has in depth been explored low thing energy balance fine molecular material mechanism, has set up new materialization, biochemical running balance reaction system.The fine molecular of the inventive method, over-saturation dissolved oxygen, superpower magnetization technology, the difficult points such as in traditional method, water body oxygen level is low, microbial biochemical reaction is incomplete are overcome, not only can be by super-saturated oxygen soluble in water, and can make aerobic microbiological amount reproduction, thereby organic decomposition in acceleration water, the nutrition source of minimizing algae.The present invention refers to above-mentioned technology in the lake water processing of river, for the solution of this world-famous puzzle of water bodies of rivers and lakes eutrophication provides brand-new improvement thinking.
The overall schematic of water magnetizing device as shown in Figure 1, magnetizing assembly comprises magnetization passage 1 and flange 2, and flange 2 is positioned at the two ends of magnetization passage 1, and wherein flange 2 plays the convenient effect connecting.Magnetization passage 1 is circular, the inner circumferential direction along magnetization passage 1 of magnetization passage 1 has high magnetic flux density magnetic field, water body when passage 1 carries out magnetic force line cutting along the axis direction of magnetization passage 1 by magnetization with certain flow rate, the water body that flows through magnetization passage 1 is magnetized, and changes because cutting magnetic line makes the character of water.
Fig. 2 is the A-A sectional view of magnetizing assembly, magnetization passage 1 comprises inner ring 4 and outer wall 5, the cross section of inner ring 4 and outer wall 5 is circle, and inner ring 4 and outer wall 5 coaxial lines, between the inner ring 4 of described magnetization passage 1 and outer wall 5, permanent magnet 3 is set, for convenience of placing, permanent magnet 3 is fan-shaped, and permanent magnet 3 can be fitted with inner ring 4; Circumferential direction and axis direction along magnetization passage 1 arrange several piece permanent magnet 3, permanent magnet 3 in magnetization in passage 1 and with it permanent magnet 3 in relative position be close to and inner ring 4 by magneticaction, between outer wall 5 and permanent magnet 3, magnetic shielding material 6 is set, the magnetic permeability of magnetic shielding material 6 is determined according to the magneticstrength of magnetizing assembly.
Fig. 3 is combination unit overall schematic, and described combination unit comprises water pump 7, magnetizing assembly 8, fine molecular device 9 and oxygenerator 10.Each device is arranged by annexation shown in Fig. 3, be put near that need to administer water body, oxygenerator 10 is connected with fine molecular device 9, while making water certain speed flow through through fine molecular device 9 by water pump 7, oxygen is dissolved in water body by fine molecular device 9, and water body is carried out to fine molecular over-saturation dissolved oxygen, through the water body of over-saturation dissolved oxygen with the certain flow rate magnetizing assembly 8 of flowing through, and carrying out magnetic force line cutting, the water body of the magnetizing assembly 8 of flowing through becomes magnetized water; Process the water body after being purified through fine molecular device 9 and magnetizing assembly 8.
Embodiment 1: fine molecular over-saturation dissolved oxygen
Fine molecular over-saturation oxygen-dissolving apparatus is to utilize physical action, make the large water clusters associating disperse to become independently individual molecule, increased the voidage between water molecules, simultaneously by after same oxygen molecule refinement, be added in the space between water molecules, make that oxygen is super-saturated to be dissolved in the water.Sewage is after this device refinement, activity, vigor and the activation capacity of material in water, G&W are improved, increase contact area, gas, solid, liquid intimate mixing and mass transfer velocity are improved, change substance reaction environment, improve interface free energy and concentration diffusion transmitting thrust, thereby effectively improved the dissolving power of various materials in water, for microbial growth and breeding provide adapt circumstance.
Water body also can reach following effect after fine molecular:
More than the concentration of oxygen in water can reach 50mg/L, tap water oxygen content can only reach 4-6mg/L, so water body oxygen concn after fine molecular is processed significantly improves, becomes over-saturation dissolved oxygen water.Water body after fine molecular over-saturation dissolved oxygen is after 1 year, the concentration of measuring residue oxygen is original more than 60%, the utilization ratio of oxygen can reach more than 95%, and conventional aeration is difficult to accomplish, as: the utilization ratio of boring aeration dissolved oxygen only can reach 5%~10%, and micro-pore aeration dissolved oxygen utilization ratio also only can reach 20%~40% left and right.This device can by oxygen over-saturation be dissolved in water, to water body create a sufficient aerobic environment, aerobic microbiological amount reproduction is conducive to the removal of various pollutents in water, is conducive to improve the ecotope of water body.
The effect of oxygen in water may be summarized as follows:
(1) the aerobic katabolism of organism
Aerobic katabolism refers under the participation of aerobic microbiological and aerobic-anaerobic microbe (heterotroph bacterium) in water, under the condition of dissolved oxygen abundance, the organism in water (representing with COD) is decomposed into CO 2and H 2o, and the metabolic process giving off energy.
(2) ammonification of organonitrogen and the nitrification of ammonia nitrogen
The in the situation that of dissolved oxygen abundance, organonitrogen ammonifying bacteria under effect, there is " aminating reaction " and be decomposed and be converted into ammonia-state nitrogen; There is again " nitration reaction " and be converted into nitrous acid nitrogen, nitrate nitrogen in ammonia-state nitrogen, then by anti-nitration reaction, nitrate nitrogen, nitrous acid nitrogen are reduced into gaseous nitrogen discharge water body under the effect of nitrifier, thereby reach the object of denitrogenation.
(3) biological phosphate-eliminating
In waste water, the form of common phosphorus is phosphoric acid salt (H 2pO 4 -, HPO 4 2-, PO 4 3-), poly-phosphate and organophosphorus.In general waste water, the phosphorus of 90% left and right exists with phos-phate forms.
PolyP bacteria absorbs the low fatty acids such as acetic acid and synthesizes a kind of salt (PHB) in cell under anaerobic state, and the decomposition of needed energy derive poly-phosphorus in thalline, has so also just caused phosphatic release.In aerobic zone, polyP bacteria is take free oxygen as electron acceptor(EA), by aerobic the PHB storing in body decomposition, and utilize and decompose the energy producing, phosphoric acid salt in excessive picked-up water body is converted into poly-phosphorus, like this in cell, aerobic phosphorous accumulating amount is greater than anaerobic phosphorus release amount, just can realize by precipitating action the object of biological phosphate-eliminating.
In a word, to the super-saturated oxygen that dissolves in the water body of eutrophication, under the acting in conjunction of above-mentioned several effects, will progressively recover the balance of nature of water body, improve the self-purification capacity of water body.
Embodiment 2: superpower magnetization
Super-strong magnetic gasifying device utilizes high magnetic flux density magnetic field, and its magnetism intensity is tens times of common ferrite magnet, and work-ing life is up to more than 10 years; And the power of unique needs allows water flow through magnetic field to be not less than necessary speed exactly when water is magnetized, does not need to increase too much energy consumption again, super-strong magnetic gasifying device does not generally need repairing, adjusts and maintains.Through putting into practice this device, the water of human body and the device of flowing through is not all worked the mischief to hydrobiont.
After magnetization is processed, there is variation because the magnetization in magnetic field makes the water molecules of macromolecular mass in water body.Micropartical polarity strengthens, and cohesive force weakens, and original longer associated molecule chain in water is truncated as shorter associated molecule chain and the distortion of charged ion, has destroyed interionic electrostatic attraction.Adsorptive power between water molecules is little, and the macromolecular mass that water is formed by 13~18 water molecules set has become the subset or the single water molecules that are assembled by 5~6 water moleculess, and the activity of water is improved greatly; The surface tension of water molecules strengthens; Water molecules seepage force strengthens, and has interfacial energy; There is the variation of angle and length in water molecules key, hydrogen bond angle reduces to 103 ° of left and right from 105 ° simultaneously; Make the potential of hydrogen of water that variation occur, pH value approximately rises 0.4~1.0.
Water body can reach following effect after magnetization:
(1) heavy-oxygen-enriched water is passed through continuously from inducedmagnetic field, in water, produce 5 × 10 -5the H of % 2o 2, this is a kind of very strong oxygenant, can make the organism direct oxidation in water decompose, thereby reduce the COD in sewage;
(2) utilize the paramagnetic field property of oxygen and the counter field of nitrogen, the nitric nitrogen existing in water is decomposed, make the form effusion water body of nitrogen element with nitrogen, thereby reduced the nutrient nitrogen of algae;
(3) ultrastrong magnetic field, in the mode of cutting magnetic line in mobile water body, makes the cell walls attenuation of algae in water, causes enchylema to run off, and causes the death of algae, thereby has reached the function except algae;
(4) sewage magnetization has very strong selecting bacteria effect, and directly sterilization rate can reach 70%~80%, but can not make all microbial deaths, especially functional microorganism, and the meeting surviving improves water body self-purification ability;
(5) mobile water forms electric current after being magnetized in water, and the existence of electric current makes the oxygen in water become active oxygen;
(6) magnetization can promote high aquatic organism growth, is conducive to ecosystem restoration, improves water body self-purification ability.
Embodiment 3: the removal of nitrogen, phosphorus
The principal element that affects lake, river algal grown is the nutrition such as nitrogen, phosphorus, and the method for the invention can be removed by following approach the nutrition such as nitrogen, phosphorus:
(1) removal of nitrogen
A. the effect of fine molecular over-saturation oxygen-dissolving apparatus
This device, in over-saturation dissolved oxygen, has reduced NH 3-N the pressure of fluid surface and with the avidity of water, thereby reduced NH 3the dissolving power of-N in water, has strengthened it and has discharged diffusibility, so just makes part NH 3-N is transferred to gas phase and is discharged from water body from liquid phase.
B. the effect of super-strong magnetic gasifying device
This device utilizes the paramagnetic field property of oxygen and the counter field of nitrogen, and the nitrate nitrogen existing in water is decomposed, and makes the form effusion water body of nitrogen element with nitrogen, thereby has reduced the nutrient nitrogen of algae.
C. the effect of aerobic microbiological
Water body, after fine molecular over-saturation dissolved oxygen, makes dissolved oxygen better be absorbed and to utilize by aerobic microbiological, has increased the quantity of aerobic microbiological, has strengthened vigor, the activity of aerobic microbiological; Improve the ability of aerobic microbiological conversion nitrogen.
(2) removal of phosphorus
A. chemical dephosphorization effect (Fe 3+and Al 3+)
In the situation that containing compared with high-solubility oxygen, be conducive to the Fe in water 2+be oxidized to Fe 3+, Fe 3+be combined with phosphoric acid salt and form the tertiary iron phosphate of indissoluble and be deposited in the middle of bed mud, the soluble phosphate in water is reduced.And Fe 3+under neutrallty condition or alkaline condition, the free state phosphorus of the ferric hydroxide colloid of generation in also can planar water, forms large flco and is deposited to the bottom.Aluminum ion (Al 3+) etc. other metal ions also have above-mentioned coagulative precipitation effect.
B. microorganism dephosphorization
The in the situation that of dissolved oxygen abundance, polyP bacteria huge uptake phosphorus, is stored in phosphorus in thalline with the form of polymerization, thereby reaches the object that phosphorus is removed from water.
(3) hydrobiont is for the removal of nitrogen, phosphorus
Because fine molecular and magnetization can promote high hydrobiological growth, increase the activity of fish body endoenzyme, thereby can increase the removal of hydrobiont for nitrogen, phosphorus.
A. food chain restructuring
---planktonic organism---food planktonic organism fish---the ichthyophagy fish that in river, have following food chain: algae.
Algophagous fish can be removed the nutritive element such as nitrogen, phosphorus in water effectively.River snail, freshwater mussel etc., also can cut down the nutritive salt such as nitrogen, phosphorus in bed mud.
B. waterplant
In treated river, waterplant ramp, its process of growth can consume the nutritive salt such as nitrogen, phosphorus a large amount of in water.
(4) removal of other pollutents
The water that contains dissolved oxygen passes through continuously from inducedmagnetic field, produces the H of 5 × 10-5% in water 2o 2, can make the organism direct oxidation in water decompose, thereby reduce the COD in sewage.After rich oxygen containing magnetic water, the activity of water oxygen increases greatly simultaneously, the degraded of COD and BOD in promotion water.
Embodiment 4:
Adopt the inventive method to process north gate, Beihai park water body, between 7 dates of June in-2011 on May 26th, 2011, use combination unit to process water body, water body sample before and after processing is sent to environmental quality inspection center of Tsing-Hua University and detects, and before processing, water sample detection report number is: CEQT-BG (W)-11052603; After processing, water sample detection report number is: CEQT-BG (W)-11060703.Test item in examining report comprises: COD, BOD 5, total phosphorus, total nitrogen, ammonia nitrogen, chlorophyll a;
Wherein the detection of every test item is according to being:
COD: rapid-digestion spectrophotometry, HJ/T399-2007;
BOD 5: water quality five-day BOD (BOD 5) mensuration dilution and inoculation method, GB/T7488-1987;
Total phosphorus: the mensuration of total phosphorus, ammonium molybdate spectrophotometry, GB/T11893-1989;
Total nitrogen: the mensuration of total nitrogen, alkaline alkaline potassium per-sulfate digestion ultraviolet spectrophotometry, GB/T11894-1989;
Ammonia nitrogen: the mensuration of ammonium, Whitfield's ointment spectrophotometry, GB/T7481-1987;
Chlorophyll a: " water and effluent monitoring analytical procedure " 2002 (the 4th edition) ultraviolet-visible spectrophotometry;
North gate, North Sea water body sampling projects test result is referring to table 1.
Table 1
Test item Detected value before processing Detected value after processing
COD(mg/L) 28.6 27.3
BOD 5(mg/L) 4.1 3.9
Total phosphorus (mg/L) 0.28 0.02
Total nitrogen (mg/L) 1.42 0.70
Ammonia nitrogen (mg/L) 0.39 0.11
Chlorophyll a (mg/L) Do not detect Do not detect
Before improvement, (on May 26th, 2011), improvement rear (on June 7th, 2011) are at north gate, the North Sea and 2, marina sampling spot sample examination.Water quality data analysis contrast before and after administering:
1. the clearance of TP is 93%, brings up to I class standard by original IV class;
2. the clearance of TN is 50.8%, more than bringing up to III class by original V class;
3. NH 3the clearance of-N is about 71.8%, brings up to I class standard by original II class;
4. chlorophyll a also has obvious removal;
Data presentation in table 1, after administering, water body obviously improves, more than water quality is brought up to III class by original V class, wherein TP, NH 3the content of-N is only 0.01mg/L, and 0.13mg/L can reach surface water environment quality I class standard.
Embodiment 5:
Adopt the inventive method to process three coaster gate upstream water quality, the treatment time is on June 21st, 1 2011 on May 25th, 2011, and table 2 is that three coaster gate upstream water correction pilot project visibilities detect data.Water turbidity refers to the obstruction degree occurring when suspended substance sees through light in water.Suspended substance in water is generally earth, sand grains, fine organism and inorganics, planktonic organism, microorganism and colloidalmaterial etc.The turbidity of water is not only relevant with the content of suspended matter in water, and relevant with their size, shape and specific refraction etc.The present invention adopts turbidimetry for Determination water turbidity, and turbidity and visibility are converted, and draws data in table 2.
Table 2
Data presentation in table:
1. water distributor place water body visibility is increased to 0.7m by original 0.55m, clear seeing the bottom after administering;
2. submersible pump place water body visibility is increased to 1.7m by original 0.45m, after improvement, substantially sees the bottom;
3. lotus ship place water body visibility is increased to the 0.8m after improvement by original 0.35m;
4. marina place water body visibility is increased to the 0.8m after improvement by original 0.4m.
Above data presentation, this region water body visibility after administering obviously improves, and all can reach water distributor and reach to the water body visibility within the scope of the 150m of downstream the expection management goal of 800mm.
In sum, by the effective control to N, P in water body, activated water molecules and oxygen molecule continue to supplement simultaneously, improve the DO content in water, for water body provides an aerobic environment, prevent algal bloom, avoid middle lower floor water body generation anaerobic digestion, Comprehensive Control indices, makes whole water body present good sense organ effect, free from extraneous odour in water, transparency obviously improves, and has contained the generation of wawter bloom, and progressively recovers the self-purification capacity of water body, improve the micro of water body, make water body keep a good order and condition steady in a long-term.
Embodiment 6:
Adopt the inventive method to process Yuyuan Lake oriental cherry Lake Water Body, between 25 dates of May in-2009 on May 15th, 2009, use combination unit to process water body, the former water water body of water body sample after treatment and oriental cherry lake sample is sent to environmental quality inspection center of Tsing-Hua University and detects, and water sample detection report number is: CEQT-BG (W)-09052504; Test item in examining report comprises: COD, BOD 5, total phosphorus, total nitrogen, ammonia nitrogen; Wherein projects detect foundation with embodiment 4, and detected result is listed in table 3.
Table 3
Figure BSA00000542095300101
The data presentation of table 3, after administering, water body obviously improves.
According to specific exemplary embodiment, invention has been described herein.It will be apparent under not departing from the scope of the present invention, carrying out to one skilled in the art suitable replacement or revise.Exemplary embodiment is only illustrative, rather than restriction to scope of the present invention, and scope of the present invention is defined by appended claim.

Claims (4)

1. repair the combination unit of eutrophication water for one kind, it is characterized in that described combination unit comprises water pump (7), magnetizing assembly (8), fine molecular device (9) and oxygenerator (10), described magnetizing assembly (8) comprises magnetization passage (1) and flange (2), and described flange (2) is positioned at the two ends of described magnetization passage (1), described magnetization passage (1) comprises inner ring (4) and the outer wall (5) that non-magnet_conductible material is made, the excircle of described inner ring (4) is provided with permanent magnet (3), the inner periphery of described outer wall (5) is provided with magnetic shielding material (6), described inner ring (4) and the same axis of outer wall (5), being shaped as of described permanent magnet (3) is fan-shaped, described permanent magnet (3) and described inner ring (4) laminating, between described permanent magnet (3) and described magnetic shielding material (6), leave space, described water pump (7), described magnetizing assembly (8) is connected with described fine molecular device (9) respectively with described oxygenerator (10).
2. a kind of combination unit of repairing eutrophication water as claimed in claim 1, is characterized in that described permanent magnet (3) and described magnetic shielding material (6) are sealed in the cavity inside that described inner ring (4), outer wall (5) and flange (2) form.
3. a kind of combination unit of repairing eutrophication water as claimed in claim 1, is characterized in that the inner magnetic induction density B value of described magnetization passage (1) is greater than 7 × 10 3gs.
4. a method of utilizing the combination unit described in claim 1 to repair eutrophication water, is characterized in that described method comprises the steps:
Step 1: water body is carried out to fine molecular over-saturation dissolved oxygen;
Step 2: in step 1 after fine molecular over-saturation dissolved oxygen water body magnetize.
CN201110205094.2A 2011-07-21 2011-07-21 Combined device and method for repairing eutrophic water Active CN102267748B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201110205094.2A CN102267748B (en) 2011-07-21 2011-07-21 Combined device and method for repairing eutrophic water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201110205094.2A CN102267748B (en) 2011-07-21 2011-07-21 Combined device and method for repairing eutrophic water

Publications (2)

Publication Number Publication Date
CN102267748A CN102267748A (en) 2011-12-07
CN102267748B true CN102267748B (en) 2014-05-21

Family

ID=45050232

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201110205094.2A Active CN102267748B (en) 2011-07-21 2011-07-21 Combined device and method for repairing eutrophic water

Country Status (1)

Country Link
CN (1) CN102267748B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110422961B (en) * 2019-08-06 2022-03-04 刘彦光 Water environment ecological restoration equipment
CN110563279B (en) * 2019-09-29 2021-03-23 中国环境科学研究院 System and method for repairing water bodies in rivers and lakes in floating type water purification field
CN111039516B (en) * 2019-12-31 2024-01-16 浙江正洁环境科技有限公司 Eutrophic water body integrated restoration device
CN113079983A (en) * 2021-04-06 2021-07-09 广西壮族自治区水产技术推广站 Facility and method for biological treatment of tail water of land-based round pond fish culture

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2091860U (en) * 1990-08-17 1992-01-01 成问好 Water magnetizer for thermos bottle
CN1803661A (en) * 2006-01-20 2006-07-19 姜庆芳 Apparatus and process for increasing water dissolved oxygen

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2091860U (en) * 1990-08-17 1992-01-01 成问好 Water magnetizer for thermos bottle
CN1803661A (en) * 2006-01-20 2006-07-19 姜庆芳 Apparatus and process for increasing water dissolved oxygen

Also Published As

Publication number Publication date
CN102267748A (en) 2011-12-07

Similar Documents

Publication Publication Date Title
Delaide et al. Aerobic and anaerobic treatments for aquaponic sludge reduction and mineralisation
CN103241908B (en) Large-scale pig farm wastewater treatment method
CN103359881B (en) Method for reducing and controlling wastewater pollution of pig farm
CN103359882B (en) Method for treating pig farm waste pollutant
CN108623099B (en) Method and device for degrading high-concentration nitrogen-content aquaculture sewage through cooperation of bacteria and algae
CN103011493B (en) Method for removing phosphate and nitrogen from hyperphosphate and high ammonia nitrogen sewage and recovering resources
CN102267748B (en) Combined device and method for repairing eutrophic water
CN106430820A (en) Biological treatment device and process for high ammonia-nitrogen pig-raising biogas slurry
CN107572725A (en) A kind of pig farm breeding wastewater ecological treatment method and system
CN101386823B (en) Special effect anaerobic denitrifying bacterium and waste water processing method using thereof
CN105585210A (en) Novel technology for treating aquaculture wastewater of fungus-aquatic plant symbiotic system
Sarfraz et al. Evaluation of Desmodesmus subspicatus for the treatment of wastewater
CN103626302B (en) The sewage water treatment method that a kind of denitrogenation dephosphorizing bacterial classification On-line testing is cultivated and tamed
Al Ahmed Dairy wastewater treatment using microalgae in Karbala city–Iraq
CN116969607A (en) Compound dominant microorganism black and odorous water treatment system
Soroosh et al. Influence of hydraulic retention time on municipal wastewater treatment using microalgae-bacteria flocs in sequencing batch reactors
CN103553236B (en) Process system for removing ammonia nitrogen/alga in surface water by enhancing conventional treatment
Shi et al. Pharmaceutical and personal care products (PPCPs) degradation and microbial characteristics of low-temperature operation combined with constructed wetlands
CN104529064A (en) Eel cultivation recirculating water treatment system
Liu et al. Microalgae-bacteria tandem-type ponds simultaneously removing ammonia nitrogen and phosphorus towards municipal wastewater advanced treatment
CN105417732A (en) Method and application for using compound microorganisms for landfill leachate treatment
CN210620525U (en) Water-fertilizer co-production device for breeding manure
CN103508564A (en) Embedded immobilized microorganism deep denitrification reactor and method
CN102060389A (en) Composite microecological preparation capable of degrading nitrites in water body rapidly
CN106967642A (en) A kind of water remediation method based on Composite Photosynthetic Bacteria preparation

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
EE01 Entry into force of recordation of patent licensing contract

Application publication date: 20111207

Assignee: BEIJING HUAN ER KANG TECHNOLOGY DEVELOPMENT Co.,Ltd.

Assignor: Hu Naiwei

Contract record no.: 2014990000618

Denomination of invention: Combined device and method for repairing eutrophic water

Granted publication date: 20140521

License type: Exclusive License

Record date: 20140805

LICC Enforcement, change and cancellation of record of contracts on the licence for exploitation of a patent or utility model
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20230419

Address after: 100102 North Zone 808, 7th Floor, Building 122, Nanhu East District, Chaoyang District, Beijing

Patentee after: Beijing Dayu Huimin Environmental Technology Co.,Ltd.

Address before: 100071 No. 62, sports road, Fengtai Town, Beijing, Fengtai District

Patentee before: Hu Naiwei