CN118164650B - Calcium bloom deposition source water strengthening device - Google Patents
Calcium bloom deposition source water strengthening device Download PDFInfo
- Publication number
- CN118164650B CN118164650B CN202410585427.6A CN202410585427A CN118164650B CN 118164650 B CN118164650 B CN 118164650B CN 202410585427 A CN202410585427 A CN 202410585427A CN 118164650 B CN118164650 B CN 118164650B
- Authority
- CN
- China
- Prior art keywords
- water
- strengthening
- flow
- calcium
- unit
- 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
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 275
- 238000005728 strengthening Methods 0.000 title claims abstract description 153
- 239000011575 calcium Substances 0.000 title claims abstract description 69
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 title claims abstract description 67
- 229910052791 calcium Inorganic materials 0.000 title claims abstract description 66
- 230000008021 deposition Effects 0.000 title claims abstract description 33
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 claims abstract description 120
- 239000002245 particle Substances 0.000 claims abstract description 107
- 229910000019 calcium carbonate Inorganic materials 0.000 claims abstract description 59
- 238000007872 degassing Methods 0.000 claims abstract description 39
- 230000001965 increasing effect Effects 0.000 claims abstract description 39
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims abstract description 32
- 229910002092 carbon dioxide Inorganic materials 0.000 claims abstract description 16
- 239000001569 carbon dioxide Substances 0.000 claims abstract description 15
- 238000005286 illumination Methods 0.000 claims abstract description 15
- 238000009210 therapy by ultrasound Methods 0.000 claims description 20
- 238000010438 heat treatment Methods 0.000 claims description 17
- 239000007921 spray Substances 0.000 claims description 14
- 238000009423 ventilation Methods 0.000 claims description 14
- 230000008093 supporting effect Effects 0.000 claims description 11
- 239000000463 material Substances 0.000 claims description 10
- 239000011148 porous material Substances 0.000 claims description 10
- 230000002708 enhancing effect Effects 0.000 claims description 8
- 230000000903 blocking effect Effects 0.000 claims description 7
- 238000005070 sampling Methods 0.000 claims description 7
- 229920000295 expanded polytetrafluoroethylene Polymers 0.000 claims description 5
- 239000000284 extract Substances 0.000 claims description 3
- 239000013589 supplement Substances 0.000 claims description 3
- 229920011532 unplasticized polyvinyl chloride Polymers 0.000 claims description 3
- WYTGDNHDOZPMIW-RCBQFDQVSA-N alstonine Natural products C1=CC2=C3C=CC=CC3=NC2=C2N1C[C@H]1[C@H](C)OC=C(C(=O)OC)[C@H]1C2 WYTGDNHDOZPMIW-RCBQFDQVSA-N 0.000 claims description 2
- 230000001502 supplementing effect Effects 0.000 claims 1
- 241000195493 Cryptophyta Species 0.000 abstract description 15
- 230000002349 favourable effect Effects 0.000 abstract 1
- 230000000694 effects Effects 0.000 description 16
- 238000011065 in-situ storage Methods 0.000 description 10
- 238000012360 testing method Methods 0.000 description 10
- 238000002604 ultrasonography Methods 0.000 description 10
- 230000008439 repair process Effects 0.000 description 9
- 230000015556 catabolic process Effects 0.000 description 8
- 238000006731 degradation reaction Methods 0.000 description 8
- 239000000523 sample Substances 0.000 description 8
- 230000008859 change Effects 0.000 description 7
- 230000001976 improved effect Effects 0.000 description 7
- 238000000034 method Methods 0.000 description 7
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 description 6
- 235000006508 Nelumbo nucifera Nutrition 0.000 description 5
- 240000002853 Nelumbo nucifera Species 0.000 description 5
- 235000006510 Nelumbo pentapetala Nutrition 0.000 description 5
- 230000003247 decreasing effect Effects 0.000 description 5
- 229910021532 Calcite Inorganic materials 0.000 description 4
- NIXOWILDQLNWCW-UHFFFAOYSA-N acrylic acid group Chemical group C(C=C)(=O)O NIXOWILDQLNWCW-UHFFFAOYSA-N 0.000 description 4
- 230000015572 biosynthetic process Effects 0.000 description 4
- 239000004568 cement Substances 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 230000002787 reinforcement Effects 0.000 description 4
- 230000000630 rising effect Effects 0.000 description 4
- 241000206761 Bacillariophyta Species 0.000 description 3
- 238000012544 monitoring process Methods 0.000 description 3
- 239000013049 sediment Substances 0.000 description 3
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000009395 breeding Methods 0.000 description 2
- 230000001488 breeding effect Effects 0.000 description 2
- 229910001424 calcium ion Inorganic materials 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 229910001220 stainless steel Inorganic materials 0.000 description 2
- 239000010935 stainless steel Substances 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 description 1
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 230000001174 ascending effect Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 239000010866 blackwater Substances 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 229940087373 calcium oxide Drugs 0.000 description 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000005284 excitation Effects 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 210000001503 joint Anatomy 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000002923 metal particle Substances 0.000 description 1
- 238000001000 micrograph Methods 0.000 description 1
- 239000003595 mist Substances 0.000 description 1
- 239000008239 natural water Substances 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
- 238000005192 partition Methods 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 239000012466 permeate Substances 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 230000035755 proliferation Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 238000005067 remediation Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 229910052710 silicon Inorganic materials 0.000 description 1
- 239000010703 silicon Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 238000012876 topography Methods 0.000 description 1
- 230000009466 transformation 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
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/20—Treatment of water, waste water, or sewage by degassing, i.e. liberation of dissolved gases
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/34—Treatment of water, waste water, or sewage with mechanical oscillations
- C02F1/36—Treatment of water, waste water, or sewage with mechanical oscillations ultrasonic vibrations
-
- 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
- C02F2101/10—Inorganic compounds
-
- 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
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
- C02F3/322—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae use of algae
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Physical Water Treatments (AREA)
Abstract
The invention relates to the technical field of natural landscape restoration, in particular to a calcium bloom deposition source water strengthening device, which comprises at least one water pump, wherein the water pump is arranged in a source water area and is used for extracting water in the source water area; the high-flow-rate strengthening unit is connected with the water pump and used for strengthening the flow rate of water pumped by the water pump, so that the density and the particle size of calcium carbonate particles in water flow are increased, and the primary strengthening is realized; and the temperature strengthening unit heats and degasifies the water flow strengthened by the high-flow rate strengthening unit, so that carbon dioxide gas in the water flow escapes from the water, and SIc is exponentially increased to strengthen the core. The calcium bloom deposition source water strengthening device provided by the invention improves the density, the particle size and the favorable algae density of calcium carbonate particles in source water through multistage strengthening modes such as flow velocity strengthening, temperature strengthening, ultrasonic strengthening, splash degassing strengthening, illumination strengthening and diatom strengthening modes and the like, improves SIc indexes, and further enables the calcium bloom to be effectively, scientifically and naturally repaired.
Description
Technical Field
The invention relates to the technical field of environmental remediation, in particular to a water strengthening device for a calcium bloom deposition source.
Background
The calcium bloom is chemical sediment of calcium carbonate formed by the escape of a large amount of carbon dioxide when groundwater rich in calcium and carbon dioxide approaches and is exposed to the ground surface. The calcite and aragonite are the main components of the calcite and aragonite; hard, compact, fine and crystalline, block-shaped, hollow or solid sphere-shaped, thick plate or thin layer, and fiber or concentric circular structure. The morphology of the calcium bloom is different and changeable, and the calcium bloom cone, hillock, fan, stalactite and the like are common. The rare landscapes formed by many calcareos in China, such as the world rare calcareos landscapes with the eastern distribution of the Qinghai-Tibet plateau in China, mainly comprise yellow dragon, the immortal pool, mou Nigou, conding sinter beach, black water Kalong ditch and the like, wherein the yellow dragon scenic spots of the world natural heritage are represented by the unique and absolute-beautiful calcareos color pool, beach current and waterfall of Asia.
In recent decades, a series of general non-earthquake-loss calcareous bloom evolution degradation problems such as calcareous bloom strong leakage, blackening, desertification, algae breeding and the like occur in a yellow dragon scenic spot, the trend of continuous reinforcement is provided, the core value of a natural heritage land is adversely affected, and huge general degradation of scales and landscape quality are reduced in adjacent Mou Nigou and immortal pools. How to scientifically and effectively restore, repair and care non-earthquake degradation calcareous bloom, ensure that landscape resources are continuously utilized by service people, and become a continuous social hotspot. The degradation of the calcareous landscape into unstructured damage and the in-situ natural restoration and conservation are unprecedented. The method follows the basic principle that the natural properties and natural recovery of the landscape are not affected, forms the new natural calcium bloom scientifically, safely, rapidly and effectively, and has great theoretical and application significance for suppressing the degradation and the normalized conservation of the calcium bloom landscape. The landscape source water with good quality is formed to promote the rapid formation of cementation, compactness and good morphology of the calcium bloom, and has great supporting effect on the in-situ repair and conservation of the non-vibration-loss degenerated calcium bloom.
Disclosure of Invention
The invention aims at the problems existing in the prior art and provides a water strengthening device for a calcium bloom deposition source.
In order to achieve the above purpose, the invention is realized by the following technical scheme:
the calcium bloom deposition source water strengthening device comprises at least one water pump I, wherein the water pump I is arranged in a source water area and used for extracting water in the source water area;
The high-flow-rate strengthening unit is connected with the first water pump and used for strengthening the flow rate of water pumped by the first water pump, so that the density and the particle size of calcium carbonate particles in water flow are increased, and the primary strengthening is realized;
The temperature strengthening unit heats and degasifies the water flow strengthened by the high-flow rate strengthening unit, so that carbon dioxide gas in the water flow escapes from the water, and SIc is exponentially increased to strengthen the core;
The ultrasonic strengthening unit is used for carrying out ultrasonic strengthening on the water flow subjected to the heating and degassing by the temperature strengthening unit, increasing the concentration of calcium carbonate particles in the water flow, and enabling SIc to increase exponentially so as to supplement strengthening;
The splash degassing strengthening unit is used for performing splash degassing on the water flow strengthened by the ultrasonic strengthening unit, and improving the density, the particle size and SIc index of calcium carbonate particles in the water to be core strengthening;
And the illumination strengthening unit is used for focusing and heating the surface of the water flow treated by the splash degassing strengthening unit, and improving SIc index of the water flow to supplement and strengthen.
Further, the high flow rate strengthening unit comprises a split-flow box, one side of the split-flow box is connected with the first water pump, the other side of the split-flow box is connected with a plurality of split-flow pipes, and each split-flow pipe is correspondingly connected with a shrinkage pipe.
Further, the shrinkage tube is any one or more of a straight tube, a coiled tube and an M-shaped serpentine bent tube with gradually changed thickness.
Further, the temperature strengthening unit comprises at least one heating rod, a supporting tube is covered outside the heating rod, a plurality of water permeable holes are formed in the supporting tube, a ventilation tube is covered outside the supporting tube, and a first air pump is installed on the ventilation tube.
Further, the supporting tube is made of UPVC material, and the ventilation tube is made of expanded polytetrafluoroethylene material.
Further, the ultrasonic strengthening unit comprises an ultrasonic treatment box, the ultrasonic treatment box is of a ventilation structure, at least two layers of ultrasonic vibration plates are sequentially arranged in the ultrasonic treatment box from top to bottom, the ultrasonic treatment box comprises an inner shell, a ventilation shell and an outer shell from outside to inside, a plurality of strip-shaped holes are formed in the inner shell, and a plurality of round holes are formed in the outer shell.
Further, the splash degassing strengthening unit comprises an open splash degassing pool, a plurality of spray pipes are vertically arranged in the open splash degassing pool, a water pump II is arranged at the lower end of each spray pipe, a water blocking cap is arranged at the upper end of each spray pipe, an inclined water outlet hole is formed in each water blocking cap, and the included angle between the central line of each inclined hole and the vertical direction is 120-150 degrees.
Further, the illumination strengthening unit comprises a water flowing groove, a plurality of lifting supports are arranged in the water flowing groove, and a condensing lens is arranged on each lifting support.
Further, the water pump I is also connected with a diatom strengthening unit, the diatom strengthening unit and the illumination strengthening unit are simultaneously combined into a combined groove, the diatom strengthening unit comprises a strengthening groove, a pore plate is arranged in the strengthening groove, one side of the strengthening groove is divided into a buffer groove by the pore plate, the other side of the strengthening groove is divided into a culture sampling groove, a cover plate is arranged above the strengthening groove, and a gap is reserved between the cover plate and the strengthening groove.
The invention has the beneficial effects that:
The calcium bloom deposition source water strengthening device provided by the invention gradually improves the density of calcium carbonate particles and the particle size of the calcium carbonate particles in source water by carrying out flow velocity strengthening, temperature strengthening, ultrasonic strengthening, jet splash removal, illumination strengthening and diatom strengthening on source water, improves SIc indexes and the participation of beneficial diatom in calcium bloom deposition, and forms source water with extremely strong calcium bloom restoration capability, so that the calcium bloom is effectively, scientifically and naturally restored, and has great theoretical and application significance for suppressing degradation of calcium bloom landscapes and normalizing preservation.
Drawings
FIG. 1 is a schematic diagram of a water strengthening device of a calcium bloom deposition source;
FIG. 2 is a schematic diagram of a high flow rate enhancement unit according to the present invention;
FIG. 3 is a schematic structural view of subtype two shrink tubing of the present invention;
FIG. 4 is a schematic structural view of subtype three of the shrink tube of the present invention;
FIG. 5 is an SEM photograph of calcium carbonate particles in a body of water at a flow rate of 0.5m/s according to the present invention;
FIG. 6 is an SEM photograph of calcium carbonate particles in a body of water at a flow rate of 1.0m/s according to the present invention;
FIG. 7 is an SEM photograph of calcium carbonate particles in a body of water at a flow rate of 1.5m/s according to the present invention;
FIG. 8 is an SEM photograph of calcium carbonate particles in a body of water at a flow rate of 2.0m/s according to the present invention;
FIG. 9 is a schematic diagram of a temperature enhancement unit according to the present invention;
FIG. 10 is a graph showing the effect of temperature on SIc according to the present invention;
FIG. 11 is a graph showing the effect of temperature on Ca 2+ according to the present invention;
FIG. 12 is a graph showing the effect of temperature on the particle size of source water calcium carbonate particles in accordance with the present invention;
FIG. 13 is a graph showing the effect of temperature on the bulk density of source water calcium carbonate particles in accordance with the present invention;
FIG. 14 is a schematic view of the structure of an ultrasonic reinforcement unit of the present invention;
FIG. 15 is a graph showing the total amount of CO 2 before and after ultrasound in accordance with the present invention;
FIG. 16 is a graph showing the variation of the ultrasound of the present invention before and after SIc;
FIG. 17 is a graph showing the change in density of calcium carbonate particles prior to ultrasound at the waterbody confetti (G1) of the present invention;
FIG. 18 shows the density change of calcium carbonate particles after ultrasound at the colorful pond (G1) of the water body of the invention;
FIG. 19 is a graph showing the change in density of calcium carbonate particles after ultrasound at the colorful pond (G2) of the water body of the invention;
FIG. 20 is a graph showing the change in density of calcium carbonate particles after ultrasound at the colorful pond (G2) of the water body of the invention;
FIG. 21 is a schematic view showing the structure of a splash degassing enhancement unit of the present invention;
FIG. 22 shows the first effect of carbon dioxide degassing for different pipe diameters of the spray nozzle of the present invention;
FIG. 23 shows a second effect of carbon dioxide degassing for different pipe diameters of the spray nozzle of the present invention;
FIG. 24 is a schematic view of the structure of the illumination enhancement unit of the present invention;
FIG. 25 is a schematic diagram of a diatom strengthening unit according to the present invention;
FIG. 26 variation of morphology of calcium carbonate particles in water prior to diatom fortification;
FIG. 27 morphology change of calcium carbonate particles in water after diatom strengthening;
FIG. 28 yellow dragon moon pool in situ algae symbiotic enhancement formed cement new calcium bloom map I;
FIG. 29 yellow dragon moon pool in situ algae symbiotic enhancement formed cement new calcium figure II;
FIG. 30 yellow dragon moon pool in situ algae symbiotic enhancement formed cement new calcium bloom map III;
FIG. 31 yellow dragon moon pool in situ algae symbiotic enhancement formed cement new calcium bloom map IV;
FIG. 32 is a photomicrograph of a calcium-metal particulate matter in water after strengthening in accordance with the invention;
FIG. 33 is a second photograph of a microscopic photograph of the calcium-metal particles in water after strengthening according to the present invention;
FIG. 34 is a third micrograph of calcium-containing particles in water after strengthening in accordance with the present invention;
FIG. 35 is a photograph of a microscopic view of calcium-containing particles in water after strengthening in accordance with the present invention;
FIG. 36 is a graph showing the effect of the test area of the lotus flower stand in the Shenxianchi region before repair;
FIG. 37 is a graph showing the effect of the test area of the lotus flower stand in the Shenxianchi region after repair;
FIG. 38 is a graph showing the effect of the test area of the lotus flower stand in the Shenxianchi region before repair;
FIG. 39 is a graph II showing the effect of the test area of the lotus flower stand in the Shenxianchi region after repair.
In the figure: 1-water pump I, 2-high flow rate strengthening unit, 21-split box, 22-split pipe, 23-shrinkage pipe, 24-water collecting tank, 3-temperature strengthening unit, 31-heating rod, 32-supporting pipe, 33-water permeable hole, 34-ventilation pipe, 35-air pump I, 36-high speed air flow layer, 4-ultrasonic strengthening unit, 41-ultrasonic treatment box, 411-inner shell, 412-ventilation shell, 413-outer shell, 414-air pump II, 42-ultrasonic vibration plate, 5-splash degassing strengthening unit, 51-open splash degassing tank, 52-jet pipe, 53-water pump II, 54-water blocking cap, 55-inclined hole, 6-illumination strengthening unit, 61-water flowing tank, 62-lifting bracket, 63-condensing lens, 7-water pipe, 8-electromagnetic flowmeter, 20-combination launder, 9-diatom strengthening unit, 91-strengthening tank, 92-orifice plate, 93-buffer tank, 94-culture sampling tank, 95-cover plate.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the accompanying drawings in the embodiments of the present invention.
In the description of the present application, it should be noted that the directions or positional relationships indicated by the terms "center", "upper", "lower", "left", "right", "vertical", "horizontal", "inner", "outer", etc. are based on the directions or positional relationships shown in the drawings, are merely for convenience of describing the present application and simplifying the description, and do not indicate or imply that the devices or elements referred to must have a specific orientation, be configured and operated in a specific orientation, and thus should not be construed as limiting the present application. Furthermore, the terms "first," "second," and "third" are used for descriptive purposes only and are not to be construed as indicating or implying relative importance.
Unless specifically stated or limited otherwise, the terms "mounted," "connected," and "coupled" are to be construed broadly, and may be, for example, fixedly connected, detachably connected, or integrally connected; can be mechanically or electrically connected; can be directly connected or indirectly connected through an intermediate medium, and can be communication between two elements. The specific meaning of the above terms in the present application will be understood in specific cases by those of ordinary skill in the art.
According to research, when SIc is smaller than 1, macroscopic calcium bloom deposition is actively slow, when SIc is larger than 1.1-1.2, new calcium bloom deposition is obvious, a remarkable deposition boundary line can be provided for SIc index control. SIc =1.2 has uniform control function in yellow dragon confetti pond and yellow dragon moon confetti pond, is generally the starting point of high-quality calcareous landscape, SIc is more than 1.4, and calcareous is extremely strongly deposited, and is visible in pond group at the downstream of yellow dragon confetti pond.
When the density and the grain diameter of calcium carbonate particles in water are in a low level, the natural deposition rate of the calcium bloom is low, the deposition capability of the calcium bloom is poor, and when the calcium carbonate particles are used for controlling the rapid formation of the new calcium bloom, in-situ strengthening treatment is required to be carried out on source water.
According to the in-situ test results of the yellow dragon scenic spot, the temperature, the flow rate, the flow state, the ultrasonic wave, the diatom and the like have better effects on the quality improvement of the calcium bloom source water, and are used as the technical basis of the application of the invention.
In this embodiment, the case of the research project of repairing calcium bloom in the yellow dragon scenic spot and the immortal pool scenic spot in Sichuan province is taken as an example, and the yellow dragon scenic spot has obvious quality degradation phenomenon due to the prominent degradation problems of calcium bloom blackening, desertification, strong leakage and the like, so that part of calcium bloom scenic spots are displayed. The calcium bloom blackification is caused by water loss and serious secondary problems caused by weathering, loose calcium bloom is formed, poor calcium bloom deposition is caused by extremely low index SIc, poor flow state (Fr < 1 forms subcritical flow), extremely low concentration of calcium carbonate particles in water and the like, the cementation capability of the calcium bloom deposition is extremely poor, strong leakage is caused by the fact that a shrub root system breaks the calcium bloom structure, and algae breeding is mainly caused by excitation of algae proliferation by blade leaching, low SIc index, strong degassing zone activity and the like.
The application provides a device and a method for strengthening the source water of calcium bloom deposition in order to repair the degraded calcium bloom landscape of a yellow dragon scenic spot in Sichuan province, which can form the source water with extremely high calcium bloom deposition capacity by in-situ transformation according to the basic principle that the natural attribute and natural recovery of the landscape are not affected so as to scientifically, safely, quickly and effectively form new natural calcium bloom.
Referring to fig. 1, the apparatus for enhancing water of a lime water deposition source provided by the present invention includes at least one water pump 1, wherein the water pump 1 is disposed in a source water area, extracts water in the source water area, and is disposed at a position determined according to a source water position area of a yellow dragon scenic spot, and is generally disposed at a position with a higher topography. The number and type of the water pumps 1 are also determined according to the actual water amount and other needs.
The first water pump 1 is connected with the high flow rate strengthening unit 2 through a water pipe 7, the water pipe 7 adopts a wear-resistant steel wire hose, and an electromagnetic flowmeter 8 is further arranged on the water pipe 7. The water pump 1 pumps the water in the raw water tank into the high-flow-rate strengthening unit 2, and the high-flow-rate strengthening unit 2 is arranged at the downstream position of the water pump 1 and is used for limiting the water flow and strengthening the water flow rate, so that the density and the particle size of calcium carbonate particles in the water flow are increased, and the primary strengthening is realized.
Referring to fig. 2-4, the high flow rate strengthening unit 2 includes a diversion box 21, the diversion box 21 is a closed box body and is made of transparent acrylic plates, a water inlet is formed in one side of the diversion box 21, a first water pump 1 is connected with the water inlet of the diversion box 21 through a water pipe 7, and the first water pump 1 pumps water in a source water pool into the diversion box 21. The other side of the shunt box 21 is provided with a plurality of water outlets, each water outlet is in butt joint with a shunt tube 22, and the number and caliber of the shunt tubes 22 are adjusted according to actual needs, so that the particle size and density of calcium carbonate in water flow are obviously increased to be standard. The water in the shunt box 21 enters the shunt tube 22 to realize the shunt. The water outlet of the shunt tube 22 is connected with a shrinkage tube 23, the shrinkage tube 23 is used for improving the water flow speed, the caliber of the reinforced shrinkage tube 23 is set according to actual needs, and the standard is that the particle size and the density of calcium carbonate in water flow are obviously increased.
The shrinkage tube 23 is of three types, namely a straight tube, a coiled tube and an M-shaped bent tube with gradually changed thickness, and any one of the three types can be selected according to the needs when the shrinkage tube is used, or a combination of the three types can be selected for use. The coiled pipe and the M-shaped bent pipe-shaped shrinkage pipe 23 are generally applied to a water body with very slow growth of the natural-flow underwater newly-grown calcium bloom. The water outlet of the shrinkage tube 23 is connected with a water collection tank 24, and the water collection tank 24 collects the water flow with the flow rate strengthened therein.
The high flow rate strengthening unit 2 limits the water flow, so that the water flow rate is quickly accelerated in the shrinkage tube 23, the average particle size and the density of the calcium carbonate particles in the water are synergistically increased and decreased along with the increase of the flow rate, and the average particle size and the density of the particles in the water are simultaneously increased in the range of 0.5-2.0 m/s. In order to further expand the repair field, a plurality of high flow rate reinforcing units 2 may be provided as needed.
Referring to fig. 5-8, after performing particle size statistics on SEM photographs of calcium carbonate particles in water at different flow rates, it is known that the characteristics of the experimental results of each gradient of the flow rates are consistent, and the particle size distribution of the particles in water accords with the Gauss distribution characteristics.
Wherein, the particle size of calcium carbonate in water is smaller than 2 μm at the flow rate of 0.5m/s in FIG. 5, the average particle size of 1.07 μm in water, the particle size of 98.0% of calcium carbonate in water is smaller than 3.5 μm at the flow rate of 1.0m/s in FIG. 6, the average particle size of 1.2 μm in FIG. 7, the particle size of 96.9% of calcium carbonate in water is smaller than 4 μm at the flow rate of 1.5m/s in FIG. 7, the average particle size of 2.45 μm in FIG. 8, the particle size of 96.6% of calcium carbonate in water is smaller than 4 μm at the flow rate of 2.0m/s in FIG. 8, and the average particle size of 2.23 μm in water.
Therefore, the characteristics that the average particle size and the content of the calcium carbonate particles in water are increased and decreased in a synergic manner are verified along with the increase of the flow rate, the average particle size and the content of the particles in water are increased and decreased at the same time in the range of 0.5-2.0 m/s of the flow rate, and the maximum value of the deposition capacity (SIc) is also generated in LS-3 (1.5 m/s), namely, the deposition capacity of a calcium bloom water body is improved when the flow rate is increased in a certain range, the content of the particles in water is increased, and the particle size of the particles in water is increased.
The temperature strengthening unit 3 is arranged at the downstream of the high flow rate strengthening unit 2 and is connected with the water collecting tank 24 through the water pipe 7, the water flow strengthened by the high flow rate contains a large amount of calcium carbonate particles, the water flow enters the temperature strengthening unit 3, the temperature strengthening unit 3 strengthens the temperature of the water flow, the calcium water body realizes strong CO 2 degassing, the concentration of Ca 2+ and HCO 3 - in the source water is rapidly reduced, the pH and the SIc are rapidly increased, and the density and the particle size of the calcium carbonate particles in the water are further improved.
Referring to fig. 9, the temperature strengthening unit 3 includes at least one heating rod 31, and the number of the heating rods 31 can be adjusted according to actual needs, and in this embodiment, three heating rods 31 are taken as an example.
The outer cover of the heating rod 31 is provided with a support tube 32, the support tube 32 is made of UPVC material, a plurality of water permeable holes 33 are formed in the surface of the support tube 32, water continuously enters the inside of the support tube 32 from the inlet end and then flows out from the outlet end, and in the process, the heating rod 31 heats the water in the support tube 32 to enable carbon dioxide in the water to escape and permeate out from the water permeable holes 33 formed in the surface of the support tube 32. Also disposed within the support tube 32 are a pH detector, a temperature probe, a TDS probe, and a temperature controller.
The support tube 32 is covered with a gas permeable tube 34, and the gas permeable tube 34 is made of gas permeable and waterproof material, such as expanded polytetrafluoroethylene material. In the heating and degassing process, carbon dioxide gas passes through the expanded polytetrafluoroethylene material to escape to the outer layer, the first air pump 35 is communicated with the air permeability pipe 34, the first air pump 35 is used for forming a high-speed air flow layer 36, and the carbon dioxide gas escaping from the high-speed air flow layer 36 capture is carried into the air to be released, so that the carbon dioxide degassing is realized, the concentration of calcium ions in water is reduced, the calcium carbonate particles are increased, and the SIc index is increased.
Referring to fig. 10 and 11, increasing the temperature increases the water SIc index, decreases the calcium ion concentration, and increases the calcium carbonate particles in the water. When the temperature is higher than 30 ℃, the carbon dioxide in the water body is basically completely deaerated, and SIc reaches the maximum value and is basically stable. Considering that the water temperature of the calcareous landscape area at the east edge of the Qinghai-Tibet plateau is generally not more than 20 ℃, the upper limit of the temperature strengthening unit is set to 20 ℃, and the typical temperature is 10-15 ℃.
Referring to fig. 12 and 13, increasing the temperature increases the content, size and promotes the formation of good morphology of the nascent calcium carbonate particles in the body of water. The particle size of calcium carbonate particles in water with lower concentration can reach the maximum value rapidly at low temperature (10-30 ℃), the content is continuously increased, the particle size of water with high calcium concentration (such as source spring water) is still increased at the temperature exceeding 50 ℃, and the particle size reaches the maximum at low temperature (10-30 ℃).
As the temperature increases (0-50 ℃), the average particle size of the particles in the water of the colorful tank (G1) is in an ascending trend, and the maximum particle size reaches 2.87 mu m at 50 ℃. The average particle size of the particles in the ditch water (G2) is increased firstly and then decreased, and reaches the maximum 3.28 mu m at the temperature of 10 ℃. The average particle size of the particles in the water of the Yingyue color pond (G3) is increased firstly and then decreased, and reaches the maximum of 3.26 mu m at the temperature of 10 ℃.
Along with the temperature rise (0-50 ℃), the surface density of particles in the water of the colorful tank (G1) is in a law of falling after rising, and reaches the maximum of 4079 particles/mm 2 at 10 ℃. The surface density of the particles in the ditch water (G2) is in a law of descending after rising, and the maximum density of 952 particles/mm 2 is reached at 30 ℃. The surface density of particles in the water of the lunar color pond (G3) is in a rising rule, and the maximum value of 1170/mm 2 is reached at 50 ℃. When the temperature of the colorful pond (G1) reaches 30 ℃ and 50 ℃, a large amount of white calcium carbonate particles are precipitated, which leads to the reduction of the surface density of the particles in water.
Referring to fig. 1 and 14, the ultrasonic strengthening unit 4 includes an ultrasonic treatment tank 41, the ultrasonic treatment tank 41 is connected with the temperature strengthening unit 3, the ultrasonic treatment tank 41 has a three-layer structure, including an inner casing 411, a ventilation casing 412 and an outer casing 413, which are sequentially arranged from outside to inside, the inner casing 411 is made of stainless steel, and a plurality of strip-shaped holes are formed in the inner casing 411. The outer casing 413 is an acrylic plate, and a plurality of circular holes are formed in the acrylic plate. The gas permeable housing 412 is made of expanded polytetrafluoroethylene material. On the premise of maintaining stable structure, the ultrasonic treatment box 41 timely dissipates carbon dioxide generated in the water in the ultrasonic process into the atmosphere, so as to avoid overhigh pressure. At least two layers of ultrasonic vibration plates 42 are sequentially arranged inside the ultrasonic treatment box 41 from top to bottom, ultrasonic generators are arranged on the ultrasonic vibration plates 42, and emit ultrasonic waves, so that the ultrasonic vibration plates 42 vibrate to treat water, and the density of calcium carbonate particles in water is increased. The second air pump 414 is connected with the air-permeable shell 412 and the outer shell 413, and extracts CO 2 gas positioned in the air-permeable shell 412 and the outer shell 413, so that the CO 2 forms a mixed gas flow layer outside the ultrasonic treatment box. The ultrasonic treatment box is externally connected with a monitoring box, is internally provided with a pH detector, a temperature detector and a TDS probe, and is connected with a monitoring regulator to display SIc values and regulate the frequency and the power of the ultrasonic vibration plate 42.
Referring to fig. 15, 16 and table 1, after the source water is strengthened by ultrasonic treatment with rated power of 120w for 30min, the calcite saturation index (SIc) in the water is obviously increased, the temperature is greatly increased, the Ca 2+、HCO3 -、TCO2 is reduced to different degrees, and as a result, the calcite saturation index (SIc) is obviously increased. The water SIc in the confetti pool (G1) is 1.01 to 1.49, the water SIc in the ditch (G2) is-0.03 to 0.54, the water SIc in the confetti pool (G3) is 0.71 to 1.24, and the lifting amplitude is 0.48 to 0.57. When the device is in a high-flow flowing water environment, the lifting amplitude is reduced to some extent. After the ultrasonic treatment, TCO 2 in the water body is lowered, which means that calcium carbonate particles in the water are increased, and carbon dioxide is dissipated into the atmosphere.
Please refer to fig. 17 for a graph of the density of the calcium carbonate particles before the ultrasound at the confetti (G1), and fig. 18 for a graph of the density of the calcium carbonate particles after the ultrasound at the confetti (G1). Fig. 19 is a graph of the density change of calcium carbonate particles before ultrasound at the confetti (G2), and fig. 20 is a graph of the density change of calcium carbonate particles after ultrasound at the confetti (G2). From the figure, the amount of calcium carbonate particles in the water body after ultrasonic treatment is obviously increased.
The statistics show that the density of calcium carbonate particles in the water of the confetti tank (G1) is increased from 238/mm 2 to 2687/mm 2, the density of calcium carbonate particles in the ditch water (G2) is increased from 162/mm 2 to 646/mm 2, and the density of calcium carbonate particles in the water of the confetti tank (G3) is increased from 196/mm 2 to 842/mm 2. The relation of the ultrasonic lifting rate of the density of the particles in three water bodies is as follows: the improvement rates of the confetti pool water (G1) > the confetti pool water (G3) > the ditch water (G2) are 1028 percent, 330 percent and 300 percent respectively, so that the sediment capacity and the sediment efficiency of the water body can be rapidly improved by the ultrasonic wave with the indication meaning for repairing the calcium bloom, and the water body effect on the source water with higher calcium concentration is more obvious.
Referring to fig. 1 and 21, the splash degassing strengthening unit 5 includes an open splash degassing tank 51, one end of the open splash degassing tank 51 is communicated with the ultrasonic treatment tank 41, a plurality of spray pipes 52 are vertically arranged in the open splash degassing tank 51, a water pump two 53 is arranged at the lower end of the spray pipes 52, a water blocking cap 54 is arranged at the upper end of the spray pipes, a plurality of inclined holes 55 are formed in the water blocking cap 54, and the number of the inclined holes 55 is set according to actual needs. The included angle between the central line of the inclined hole 55 and the vertical direction is 120-150 degrees. The spray pipe 52 is provided with a pH detector, a temperature detector and a TDS probe, and is connected with a monitoring regulator to timely adjust the power of the pump set.
Referring to fig. 22 and 23, the open splash degassing pool 51 drives water flow by using the second water pump 53, creates a fountain splash environment to form high-speed thin-layer water mist, increases the water-gas contact area and time, performs strong degassing of carbon dioxide, and improves the SIc index. If the 3 kinds of caliber spray pipes of 20mm, 32mm and 40mm are selected for test, under the condition of flow 1260m 3/d, the three kinds of spray pipes (20 mm, 32mm and 40 mm) have obvious promotion effect on degassing, and compared with the efficiency promotion before degassing, the method comprises the following steps: 61.9%, 62.8%, 56.3%, SIc% of the total weight of the cable is increased by 43-50%. The water quality calcium bloom deposition capability of the water entering the repair area before and after degassing is obviously improved by a typical 32mm pipe, SIc is improved by 35.1% from 1.14 to 1.54, P CO2 is obviously reduced, and the degassing efficiency is 63.7%.
Referring to fig. 1 and 24, the illumination strengthening unit 6 is connected with the splash degassing strengthening unit 5, and focuses and heats the surface of the water flow treated by the splash degassing strengthening unit 5, so as to raise the SIc index of the water flow for supplementary strengthening.
The illumination strengthening unit 6 comprises a water flowing groove 61, wherein the water flowing groove 61 is made of stainless steel materials, and one end of the water flowing groove 61 is connected with the splash degassing strengthening unit 5. The water flow channel 61 is provided with a plurality of lifting brackets 62, the lifting brackets 62 are screw rod supporting seats, and the condensing lens 63 is arranged on the screw rod supporting seats. The water flows into the water flow groove 61, and a thin water flow is formed at the bottom of the water flow groove 61, and the thickness of the thin water flow is less than or equal to 1cm. The condensing lens 63 is a Fresnel lens, the angle and the height of the lens are adjusted, the lens is focused on the surface of water flow, and heating is performed, so that the index effect of SIc is improved. The water flow channel 61 is connected to a common water channel, the side of the common water tank is connected with a sample measuring cylinder, a pH probe, a temperature probe and a TDS probe are arranged in the reactor, and accessing a monitor and displaying SIc in real time.
In short, the illumination unit utilizes the heating to strengthen the degassing process of the water body, and the core is a Fresnel lens unit, when sunlight passes through the Fresnel lens, light rays can be accumulated to form a small area (called a focus) with very high energy density, and the flowing water body can be heated at the focus.
Referring to fig. 1 and 25, the first water pump 1 is further connected with a diatom strengthening unit 9, and the diatom strengthening unit 9 and the illumination strengthening unit 6 are simultaneously combined into the converging tank 20. The diatom strengthening unit 9 comprises a strengthening groove 91, wherein a pore plate 92 is arranged in the strengthening groove 91, the pore plate 92 is a partition plate with a plate body open hole, one side of the strengthening groove 91 is divided into a buffer groove 93 by the pore plate 92, the other side of the strengthening groove 91 is divided into a culture sampling groove 94, a cover plate 95 is arranged above the strengthening groove 91, a gap is formed between the cover plate 95 and the strengthening groove 91, the height of the gap is 2-3cm, and the gap is reserved for ventilation.
The water pump 1 is connected with low-flow water flow, the water flow is sequentially buffered in the buffer tank 93 and the culture sampling tank 94, the flow speed of the water flow is reduced through the buffer tank 93, the impact force is reduced, and then the water flow enters the culture sampling tank 94, and algae grows in the culture sampling tank 94. The strengthening groove 91, the pore plate 92 and the cover plate 95 are assembled by adopting transparent acrylic plates with the thickness of 1cm, and the pore diameter of the pore plate 92 is 20mm. The yellow dragon landscape water generally contains a certain amount of diatom algae, the special throwing is not needed, the yellow dragon landscape water mainly contains the yellow algae, the boat algae and the needle bar algae, the diatom algae naturally grow on a large scale under the condition of strong sunlight, for example, the yellow dragon-reflected moon pool can form diatom-rich water through the reinforcement of algae for about 7-10 days, calcium carbonate aggregates with the particle size of tens of micrometers in the water are basically visible to naked eyes, the particle size is improved by ten times or tens of times compared with that in natural water (1-5 mu m), silicon algae mat is formed on the inner wall of a reinforced box, the thickness is about 2-5 mm, and the application scene is the condition that the flow rate of a restored and maintained field is generally 0.3-0.5 m/s.
Referring to fig. 26-31, the morphology of the calcium carbonate particles in the water before and after the diatom strengthening is changed, so that the number of the calcium carbonate particles after the strengthening is increased, the volume is increased, and the adhesion between the calcium carbonate particles is enhanced. And (3) using the in-situ reinforcement test result of the Huanglong Yue color pool, wherein the test conditions are that the flow rate is 0.34-0.51 m/s, the average flow rate is 0.43m/s, the supercritical water flows are all Fr > 1.2, and the test period is 60d. Under the low flow rate environment, the deposition rate of the calcium bloom still maintains at a higher level (about 6 mm/a) due to the participation of the diatom, and is even stronger than the typical high flow rate (1-2 m/s) environment (4-5 mm/a). The extracellular division of the diatom is used for promoting the formation and cementation of large calcium bloom particles and further improving the deposition rate of the calcium bloom.
Working principle:
When the water pump 1 is used, water in a source water area is pumped by the water pump 1 and is respectively sent to the diatom strengthening unit 9 and the high-flow-rate strengthening unit 2, water flow enters from the high-flow-rate strengthening unit 2 and sequentially passes through the temperature strengthening unit 3, the ultrasonic strengthening unit 4, the splash degassing strengthening unit 5 and the illumination strengthening unit 6 for strengthening and then is gathered into the flow combining groove 20, and the diatom strengthening unit 9 is used for strengthening the source water and then gathered into the flow combining groove 20. The reinforced source water promotes the density, the particle size and SIc index of calcium carbonate particles in the rising water, and can realize the rapid restoration of the calcium bloom. Referring to fig. 32-35, after the water quality of SIc is prepared, caCO 3 particles in the water body are subjected to various classical and denser calcites, which are in the forms of cubes, spindles, zhong Ruzhuang and the like, and have an average diameter of about 5 μm. 36-39, the repairing effect of the test area of the Shenxianchi lotus flower table is quite obvious by comparison.
It should be noted that, the application scenario of the present invention is as follows:
General scenario: the method is applied to source water regulation and control for blackening, strong leakage and calcium bloom and poor sedimentation, an algae strengthening unit is not started generally, source water SIc is generally more than 1.2, source water SIc is generally more than 1.4, strengthening units are comprehensively configured according to source water inlet water quality (calcium concentration, SIc index) and flow, the strengthening units are started step by step, and when SIc value reaches a preset target value, a lower unit is not started.
Special scenarios: the method comprises the steps of (1) starting a flow velocity strengthening and diatom strengthening unit to form low-flow high-diatom source water, forming a thin layer (not more than 1 cm) beach flow, and rapidly cementing loose calcium bloom by using large calcium carbonate particles and extracellular division necessities of diatoms.
The foregoing is a further detailed description of the invention in connection with the preferred embodiments, and it is not intended that the invention be limited to the specific embodiments described. It will be apparent to those skilled in the art that several simple deductions or substitutions may be made without departing from the spirit of the invention, and these should be considered to be within the scope of the invention.
Claims (8)
1. The utility model provides a calcium bloom deposition source water strengthening device which characterized in that: comprising
At least one water pump I (1), wherein the water pump I (1) is arranged in the source water area and extracts water in the source water area;
the high-flow-rate strengthening unit (2) is connected with the first water pump (1) and is used for strengthening the flow rate of water extracted by the first water pump (1) so as to increase the density and the particle size of calcium carbonate particles in water flow and realize primary strengthening;
a temperature strengthening unit (3) for heating and degassing the water flow strengthened by the high-flow-rate strengthening unit (2) so as to enable carbon dioxide gas in the water flow to escape from the water, wherein SIc is exponentially increased and is core strengthening;
The ultrasonic strengthening unit (4) is used for carrying out ultrasonic strengthening on the water flow which is heated and degassed by the temperature strengthening unit (3), so that the density of calcium carbonate particles in the water flow is increased, and the SIc index is increased to supplement strengthening;
A splash degassing strengthening unit (5) for performing splash degassing on the water flow strengthened by the ultrasonic strengthening unit (4) to improve the density, the particle size and SIc index of calcium carbonate particles in the water, and the strengthening is core strengthening;
the illumination strengthening unit (6) is used for focusing and heating the surface of the water flow treated by the splash degassing strengthening unit (5) and improving SIc index of the water flow for supplementing and strengthening;
The high-flow-rate strengthening unit (2) comprises a flow distribution box (21), one side of the flow distribution box (21) is connected with a first water pump (1), the other side of the flow distribution box is connected with a plurality of flow distribution pipes (22), and each flow distribution pipe (22) is correspondingly connected with a shrinkage pipe (23).
2. The apparatus for enhancing water of a calcium bloom deposition source as claimed in claim 1, wherein: the shrinkage tube (23) is any one or more of a straight tube, a coiled tube and an M-shaped serpentine bent tube with gradually changed thickness.
3. The apparatus for enhancing water of a calcium bloom deposition source as claimed in claim 1, wherein: the temperature strengthening unit (3) comprises at least one heating rod (31), a supporting tube (32) is covered outside the heating rod (31), a plurality of water permeable holes (33) are formed in the supporting tube (32), a ventilation tube (34) is covered outside the supporting tube (32), and an air pump I (35) is installed on the ventilation tube (34).
4. A bloom deposition source water enhancing apparatus as claimed in claim 3, wherein: the supporting tube (32) is made of UPVC material, and the ventilation tube (34) is made of expanded polytetrafluoroethylene material.
5. The apparatus for enhancing water of a calcium bloom deposition source as claimed in claim 1, wherein: the ultrasonic strengthening unit (4) comprises an ultrasonic treatment box (41), the ultrasonic treatment box (41) is of a ventilation structure, at least two layers of ultrasonic vibration plates (42) are sequentially arranged in the ultrasonic treatment box (41) from top to bottom, an ultrasonic generator is arranged on each ultrasonic vibration plate (42), the ultrasonic treatment box (41) sequentially comprises an inner shell (411), a ventilation shell (412) and an outer shell (413) from outside to inside, a plurality of strip-shaped holes are formed in the inner shell (411), and a plurality of round holes are formed in the outer shell (413).
6. The apparatus for enhancing water of a calcium bloom deposition source as claimed in claim 1, wherein: the splash degassing strengthening unit (5) comprises an open splash degassing pool (51), a plurality of spray pipes (52) are vertically arranged in the open splash degassing pool (51), a water pump II (53) is arranged at the lower end of each spray pipe (52), a water blocking cap (54) is arranged at the upper end of each spray pipe, inclined holes (55) are formed in the water blocking caps (54), and the included angle between the central line of each inclined hole (55) and the vertical direction is 120-150 degrees.
7. The apparatus for enhancing water of a calcium bloom deposition source as claimed in claim 1, wherein: the illumination strengthening unit (6) comprises a water flowing groove (61), a plurality of lifting supports (62) are arranged in the water flowing groove (61), and a condensing lens (63) is arranged on each lifting support (62).
8. The apparatus for enhancing water of a calcium bloom deposition source as claimed in claim 1, wherein: the water pump I (1) is also connected with a diatom strengthening unit (9), the diatom strengthening unit (9) and the illumination strengthening unit (6) are simultaneously combined with a combining groove (20), the diatom strengthening unit (9) comprises a strengthening groove (91), a pore plate (92) is arranged in the strengthening groove (91), the pore plate (92) separates one side of the strengthening groove (91) into a buffer groove (93), the other side of the strengthening groove is separated into a culture sampling groove (94), a cover plate (95) is arranged above the strengthening groove (91), and a gap is reserved between the cover plate (95) and the strengthening groove (91).
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202410585427.6A CN118164650B (en) | 2024-05-13 | 2024-05-13 | Calcium bloom deposition source water strengthening device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202410585427.6A CN118164650B (en) | 2024-05-13 | 2024-05-13 | Calcium bloom deposition source water strengthening device |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN118164650A CN118164650A (en) | 2024-06-11 |
| CN118164650B true CN118164650B (en) | 2024-08-13 |
Family
ID=91347180
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202410585427.6A Active CN118164650B (en) | 2024-05-13 | 2024-05-13 | Calcium bloom deposition source water strengthening device |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN118164650B (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN118619391B (en) * | 2024-08-08 | 2024-10-18 | 四川省地质环境调查研究中心 | In-situ natural calcium bloom model manufacturing device |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN219839519U (en) * | 2023-05-19 | 2023-10-17 | 四川省地质矿产勘查开发局成都水文地质工程地质中心 | Water strengthening device of calcium bloom deposition source based on ultrasonic excitation |
Family Cites Families (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2360033A (en) * | 2000-03-06 | 2001-09-12 | 3P Technologies Ltd | Precipitating aragonite calcium carbonate |
| US20030161894A1 (en) * | 2001-09-05 | 2003-08-28 | 3P Technologies Ltd. | Precipitated aragonite and a process for producing it |
| FI121232B (en) * | 2007-12-14 | 2010-08-31 | Timo Olavi Imppola | Process and apparatus for speeding up continuous production of precipitated calcium carbonate |
| ME02142B (en) * | 2011-07-22 | 2015-10-20 | Omya Int Ag | MICRONIZED CaC03 SLURRY INJECTION SYSTEM FOR THE REMINERALIZATION OF DESALINATED AND FRESH WATER |
| CN103183370B (en) * | 2013-04-18 | 2014-11-12 | 浙江工业大学 | Method for preparing industrial ultra-fine activated calcium carbonate from carbide slag |
| CN111661930B (en) * | 2020-06-08 | 2022-09-27 | 浙江工业大学 | Method for repairing arsenic pollution in high-saline-alkali water body by using calcium ion enhanced blue algae-phycomycetes biomembrane |
| CN115613542A (en) * | 2022-11-09 | 2023-01-17 | 成都理工大学 | Method for promoting calcium bloom restoration by submerged plants |
| CN116282544A (en) * | 2022-12-08 | 2023-06-23 | 成都理工大学 | Method for promoting rapid precipitation of calcium bloom crystals by utilizing algae |
| CN219923355U (en) * | 2023-06-16 | 2023-10-31 | 四川省地质矿产勘查开发局成都水文地质工程地质中心 | Long-acting underwater jet device for natural restoration of colored pond in calcium bloom |
-
2024
- 2024-05-13 CN CN202410585427.6A patent/CN118164650B/en active Active
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN219839519U (en) * | 2023-05-19 | 2023-10-17 | 四川省地质矿产勘查开发局成都水文地质工程地质中心 | Water strengthening device of calcium bloom deposition source based on ultrasonic excitation |
Non-Patent Citations (1)
| Title |
|---|
| "钙华沉积的水化学控制因素分析及天津王四井钙华形成的模拟研究";郭小娟;《中国优秀硕士学位论文全文数据库 基础科学辑》;20110815;第2011年卷(第8期);第A012-6页 * |
Also Published As
| Publication number | Publication date |
|---|---|
| CN118164650A (en) | 2024-06-11 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN118164650B (en) | Calcium bloom deposition source water strengthening device | |
| CN101676226A (en) | Three-dimensional waterbody circular oxygenation purification plant and method | |
| CN108479188B (en) | Directional sand settling and discharging filtering device with multi-layer diversion baffle and method thereof | |
| CN206494734U (en) | A kind of gas can push away water eddy flow sewage collection system | |
| KR20100113688A (en) | Seawater intake system using sand layer of sea as filter | |
| CN105217811B (en) | It is a kind of to be used to improve the Waterwheel-type strengthening and processing device of water quality | |
| CN206970354U (en) | A kind of collapsible underground water pollution prosthetic device | |
| CN206467758U (en) | Rainwater recycle reutilization system structure | |
| CN104230099A (en) | Self-purification landscape water pool | |
| CN204746721U (en) | A push away a class oxygen boosting formula view fountain system for water ecological remediation | |
| CN201264941Y (en) | Three-dimensional water circulation oxygenation purification apparatus | |
| CN106082469B (en) | A kind of silt of drip irrigation system regulates and controls method step by step | |
| CN110498519A (en) | A kind of stagnant slow flow water bodies gas stripping type deep-well pressurization control algae of shallow-layer and decontamination dyeing equipment | |
| CN209702362U (en) | Electrolytic air-floating machine | |
| CN109694147A (en) | The Non-energy-consumption of domestic water takes net integrated apparatus | |
| CN207918607U (en) | A kind of efficient radial-flow sedimentation basin of sewage disposal | |
| CN102910703A (en) | Ultrasonic air floatation system | |
| CN109231612A (en) | A kind of mountain torrents are taken precautions against natural calamities hydraulic engineering device | |
| CN210261448U (en) | Trapezoidal composite flow artificial rapid infiltration tank and sewage treatment system thereof | |
| CN204185344U (en) | Integrated sewage treating apparatus | |
| CN104261710A (en) | Desalting pond and method for desalting sea sand | |
| KR102388959B1 (en) | Deep learning system for control and operation of multiple mobile water quality improvement devices | |
| CN107555652A (en) | The micro-nano molecular sieve algae water of cofferdam type of original position collection blue-green alga bloom is same to control system | |
| CN209210591U (en) | It is a kind of to intercept purification device for the multistage of suspended particulate organic matter | |
| CN118518420B (en) | Tidal bore tide head high-frequency layered water and sand sampling method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |