CN115259250A - Combined technology treatment method for water pollution treatment - Google Patents

Combined technology treatment method for water pollution treatment Download PDF

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Publication number
CN115259250A
CN115259250A CN202210829415.4A CN202210829415A CN115259250A CN 115259250 A CN115259250 A CN 115259250A CN 202210829415 A CN202210829415 A CN 202210829415A CN 115259250 A CN115259250 A CN 115259250A
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chlorine dioxide
subsystem
water
sodium hypochlorite
permanganate
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CN115259250B (en
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纪银传
陈剑评
林业
曾华屹
刘伟强
张清煜
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Jinjiang Huatian Municipal Engineering Co ltd
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Jinjiang Huatian Municipal Engineering Co ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/76Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/203Iron or iron compound
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/206Manganese or manganese compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/002Construction details of the apparatus
    • C02F2201/007Modular design
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/005Processes using a programmable logic controller [PLC]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/11Turbidity
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/29Chlorine compounds

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  • 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)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

The invention belongs to the technical field of water treatment, and particularly relates to a combined technical treatment method for water pollution treatment. The combined technical treatment method for water pollution treatment adopts a combined technical method, integrates three subsystems of chlorine dioxide-sodium hypochlorite-permanganate into one combined feeding central control module, adopts various combined feeding technical schemes aiming at the different and same conditions of iron and manganese pollution indexes of water source water, and simultaneously and accurately adjusts different feeding point positions, different feeding sequences and different feeding amounts, thereby realizing the effects of removing different pollution indexes, reducing byproducts and ensuring the stable and standard reaching of discharged water.

Description

Combined technology treatment method for water pollution treatment
Technical Field
The invention relates to the technical field of water treatment, in particular to a combined technical treatment method for water pollution treatment.
Background
Urban drinking water sources are usually taken from large water conservancy facilities such as rivers, lakes, reservoirs and the like, and water of the water sources is conveyed to various waterworks as water sources through approaches such as riverways, open channels, hidden culverts and the like; during each summer rainstorm period, the water quality of the source water exceeds the standard due to the fact that the iron and manganese indexes of the source water exceed the limit requirements of III indexes of surface water environmental quality standard, if the iron and manganese indexes of the source water exceed the limit values of the III indexes, a water purification plant does not timely take scientific and efficient emergency treatment measures to deal with the problem, the quality of tap water outlet water of a water supply enterprise exceeds the standard, and the specific expression is that: indexes of discharged water, pipe network water and tap water outlet color of a user terminal, such as 'yellowing', 'iron and manganese' are seriously beyond the index limit of GB5749-2022 sanitary Standard for Drinking Water, and the water quality safety of urban water supply cannot be guaranteed;
aiming at the specific pollution of iron and manganese generated in the water period of a water source, six emergency disposal methods for single water pollution are adopted by the same lines at home and abroad:
the method is effective for low-concentration iron and manganese pollution indexes, has no obvious effect on high-concentration iron and manganese pollution indexes, and can naturally lose efficacy after long-time use;
secondly, iron and manganese indexes are removed by adopting sodium hypochlorite preoxidation of a disinfectant owned by a water plant, the method is effective in removing low-concentration iron and manganese pollution indexes, and is basically ineffective when the iron and manganese indexes are higher; when sodium hypochlorite is used as a disinfectant in a water plant, the sodium hypochlorite is used as an oxidant for removing iron and manganese, so that the total dosage of the sodium hypochlorite is increased rapidly, and the index of chlorate which is a disinfection byproduct of factory water exceeds the standard;
thirdly, the iron and manganese indexes are removed by increasing the adding amount of the flocculating agent, the method has low removal rate of the pollution indexes of iron and manganese in the water source water, and the pollution indexes with high concentration cannot be effectively solved;
fourthly, a chlorine dioxide pre-oxidation method is adopted to remove the iron and manganese indexes, when chlorine dioxide is used as an 'iron and manganese' remover, chlorate and chlorite byproducts are synchronously generated, the effect is good when the pollution indexes of low-concentration 'iron and manganese' are treated, and the indexes of the chlorate and the chlorite, which are sterilization byproducts of the factory water, exceed the standard when the pollution indexes of high-concentration 'iron and manganese' are treated;
fifthly, the indexes of iron and manganese are removed by adopting a water flow through stage natural falling and blast aeration oxidation method, the method has certain effect on the pollution indexes of low-concentration iron and manganese, and basically has no removal effect on the pollution indexes of high-concentration iron and manganese;
sixthly, the iron and manganese indexes are removed by adopting an ozone oxidation method, and in the method, ozone purchase price is high, equipment investment is large, operation in the using process is complex, and a large operation safety risk is caused;
when the specific pollution accidents of iron and manganese generated in the water source water period are treated in China, the continuous and effective operation of a disinfection process is hardly ensured by adopting the traditional single-flow oxidation disinfection technology, the iron and manganese pollution is removed and treated by adopting the single-flow technology, an intelligent management system is not configured, the aims of accuracy, effectiveness, safety and convenience are not achieved in the specific implementation process, and the problems of the exceeding standard of iron and manganese, the disinfection by-product problem and the disinfection allowance index of factory water in the water supply industry cannot be synchronously solved.
Disclosure of Invention
The invention provides a combined technical treatment method for water pollution control based on the technical problems that the existing water treatment can not synchronously solve the problems of excessive ferro-manganese, disinfection by-products and the disinfection allowance index of factory water in the water supply industry.
The invention provides a combined technology treatment method for water pollution treatment, which comprises a central integrated artificial intelligence system, a chlorine dioxide dosing subsystem, a sodium hypochlorite dosing subsystem and a permanganate dosing subsystem, wherein the central integrated artificial intelligence system carries out intelligent control management on the chlorine dioxide dosing subsystem, the sodium hypochlorite dosing subsystem and the permanganate dosing subsystem.
Preferably, the method further comprises the following steps:
the central integrated artificial intelligence system comprises an online information acquisition module, an information gathering visual interface module, an accurate feeding control module, a combined feeding central control module, a safety early warning protection module and an automatic report generation module;
collecting turbidity values, residual chlorine values, pH values, residual chlorine dioxide values and alarm instrument data in the working processes of the chlorine dioxide dosing subsystem, the sodium hypochlorite dosing subsystem and the permanganate dosing subsystem through the online information collecting module, and displaying the data collected by the online information collecting module through the information summarizing visual interface module;
step three, pass through the accurate control module of throwing is right chlorine dioxide adds the subsystem into chlorine dioxide add the subsystem with the permanganate adds the subsystem and carries out the accurate control of throwing, it is right to jointly add central control module chlorine dioxide that chlorine dioxide adds the subsystem and throws sodium hypochlorite that the subsystem was thrown with the real-time condition of throwing of permanganate that the subsystem was thrown with the permanganate carries out intelligent analysis, jointly add central control module with the accurate control module of throwing is mutually supported, and intelligent control or the real-time volume of throwing of adjustment chlorine dioxide, sodium hypochlorite and permanganate.
Preferably, the chlorine dioxide dosing subsystem comprises a chlorine dioxide generator, a first digital metering pump, a first intelligent control system, a first raw material storage tank and a first chlorine leakage alarm, wherein the chlorine dioxide generator stores liquid hydrochloric acid and liquid sodium chlorate in the first raw material storage tank respectively.
Preferably, the first digital metering pump precisely meters the hydrochloric acid and the sodium chlorate and then conveys the hydrochloric acid and the sodium chlorate to a reaction kettle of a chlorine dioxide generator, the chlorine dioxide generator heats the hydrochloric acid and the sodium chlorate through a water bath to mix the hydrochloric acid and the sodium chlorate to generate chlorine dioxide gas, and the chlorine dioxide gas overflowing from the reaction kettle of the chlorine dioxide generator is carried by negative pressure generated by a water ejector in the chlorine dioxide generator, mixed with water flow and conveyed to a feeding point of the central integrated artificial intelligence system;
the first intelligent control system controls the adding amount of hydrochloric acid and sodium chlorate by adjusting the operating frequency of the first digital metering pump, the first chlorine leakage alarm instrument timely feeds back to the central integrated artificial intelligent system when monitoring the leakage of chlorine dioxide gas, and the central integrated artificial intelligent system reminds operators on duty to take emergency measures by sound-light alarm and carries out shutdown or pressure reduction protection measures on the chlorine dioxide adding subsystem.
Preferably, the sodium hypochlorite adding subsystem comprises a second digital metering pump, a second raw material storage tank, a second intelligent control system, a second chlorine leakage alarm and an emergency recovery device, and the second raw material storage tank stores a sodium hypochlorite solution diluted to 5% in concentration;
through second intelligence control system is through control the operating frequency of second digital measuring pump carries out the accuracy to sodium hypochlorite's the volume of throwing with throwing, when the second leaks the chlorine alarm appearance and monitors sodium hypochlorite and leak, in time feed back to integrated artificial intelligence system of central authorities, integrated artificial intelligence system of central authorities reminds the person on duty to take emergency measures through audible-visual alarm, and control sodium hypochlorite dosing subsystem stall, trigger automatic safety device, emergent recovery unit makes the sodium hypochlorite of leaking flow into the recovery pond through the mode that gravity flowed and carries out the safety recovery when sodium hypochlorite takes place to leak by a large scale.
Preferably, the permanganate adding subsystem comprises a third digital metering pump, a third raw material storage tank, a permanganate leakage monitoring and treating module and a third intelligent control system, wherein the third raw material storage tank stores 3% permanganate solution;
through third intelligence control system is through control the operating frequency of third digital metering pump carries out the accuracy to the volume of throwing of permanganate and throws, when permanganate leakage is monitored and is dealt with the module and monitor the permanganate and leak, in time feed back to central integrated artificial intelligence system, central integrated artificial intelligence system reminds the person on duty to take emergency measures through audible and visual alarm, and control permanganate throwing subsystem stop operation triggers automatic safety device.
Preferably, in the process of executing the first step to the third step, when a water quality online instrument detects that the iron index concentration of raw water is between 0.2mg/L and 0.4mg/L and the manganese index concentration is between 0.1mg/L and 0.2mg/L, the central integrated artificial intelligence system analyzes source water to obtain that the source water is slightly polluted, the central integrated artificial intelligence system sends an instruction to control the chlorine dioxide adding subsystem to operate independently, an adding point is preset to be a front filtering end and a rear filtering end, firstly, 1.0 to 2.0mg/L of chlorine dioxide is added to the front filtering end, secondly, 2.0 to 1.0mg/L of chlorine dioxide is added to the rear filtering end, and the total adding amount of the chlorine dioxide before and after filtering is controlled to be less than or equal to 3mg/L;
after chlorine dioxide adding operation is executed, the central integrated artificial intelligence system judges and analyzes the values of collected filtered water on-line chlorine dioxide, on-line turbidity, on-line manganese indexes and on-line iron indexes, and the standards of the values of the filtered water on the chlorine dioxide, turbidity, iron and manganese indexes are as follows: chlorine dioxide is less than or equal to 0.1mg/L, turbidity is between 0.3 and 0.6NTU, iron is between 0.1 and 0.2mg/L, and manganese is between 0.05 and 0.1mg/L;
when the index values of chlorine dioxide, turbidity, iron and manganese in the filtered water all accord with preset values, the central integrated artificial intelligence system controls a chlorine dioxide adding subsystem to execute the current operation to form a composite ring period without changing the adding point and adding amount of the chlorine dioxide;
when the index values of chlorine dioxide, turbidity, iron and manganese of the filtered water deviate from the preset requirements, the chlorine dioxide adding subsystem recognizes that the adding amount is insufficient, and sends an up-regulation instruction to the first digital metering pump.
Preferably, the water quality indexes after the adjustment of the compound ring period of the chlorine dioxide adding subsystem are respectively that the chlorine dioxide is less than or equal to 0.1mg/L, the turbidity is between 0.6 and 1.0NTU, the iron is between 0.2 and 0.3mg/L and the manganese is between 0.1 and 0.2mg/L, which indicates that the iron and manganese pollution degree of raw water is increased;
entering next-step upgrading management and control operation, analyzing the source water by the combined feeding central control module to obtain that the source water is moderately polluted, starting the sodium hypochlorite feeding subsystem in a self-adaptive and synchronous mode by the combined feeding artificial intelligence module, stopping feeding of chlorine dioxide at the rear end of the filter synchronously, automatically switching a feeding point to be the feeding of the chlorine dioxide at the front end of the filter by the central integrated artificial intelligence system, feeding the chlorine dioxide at the rear end of the filter by the central integrated artificial intelligence system, and firstly feeding the chlorine dioxide at the front end of the filter, wherein the feeding amount is controlled to be 2.9 mg/L-3.8 mg/L; secondly, adding sodium hypochlorite at the rear end of the filter, wherein the adding amount is controlled to be 2.2-1.8 mg/L;
the central integrated artificial intelligence system is used for collecting the index values of chlorine dioxide, turbidity, iron and manganese of the filtered water in real time: residual chlorine is less than or equal to 0.1mg/L, turbidity is between 0.3 and 0.6NTU, iron is between 0.1 and 0.2mg/L, manganese is between 0.05 and 0.1mg/L, and the sodium hypochlorite adding subsystem sends an up-regulation instruction to the second digital metering pump when the sodium hypochlorite adding subsystem recognizes that the adding amount is insufficient.
Preferably, the water quality indexes after the period adjustment of the compound ring added by the chlorine dioxide adding subsystem and the sodium hypochlorite adding subsystem are respectively that the chlorine dioxide is less than or equal to 0.1mg/L, the turbidity is between 0.6 and 1.0NTU, the iron is between 0.2 and 0.3mg/L and the manganese is between 0.1 and 0.2mg/L, which indicates that the iron and manganese pollution degree of raw water is further increased;
continuing to upgrade the management and control operation in the next step, analyzing the source water quality index by the central integrated artificial intelligence system, identifying that the source water is heavily polluted, and showing that the problem cannot be solved by the scheme of matching the chlorine dioxide dosing subsystem and the sodium hypochlorite dosing subsystem controlled by the combined dosing central control module, starting the permanganate dosing subsystem by the combined dosing central control module in a self-adaptive increasing manner, and automatically switching the dosing point to: adding permanganate at the front end of flocculation, adding chlorine dioxide at the front end of filtration, and adding sodium hypochlorite at the rear end of filtration, wherein in the first step, the permanganate is added at the front end of flocculation, and the adding amount is controlled to be 0.5-3.0 mg/L; secondly, adding chlorine dioxide at the front end of the filter, wherein the total adding amount is controlled to be less than or equal to 3.0mg/L; thirdly, adding sodium hypochlorite at the rear end of the filter, wherein the total adding amount is controlled to be less than or equal to 2.5mg/L;
the central integrated artificial intelligence system carries out comprehensive analysis and dynamic adjustment according to the index values of filtered water chlorine dioxide, turbidity, iron and manganese collected in real time: if the chlorine dioxide in the filtered water index is less than or equal to 0.1mg/L, the turbidity is between 0.1 and 0.2NTU, the iron is between 0.05 and 0.1mg/L, the manganese is between 0.02 and 0.05mg/L, the preset requirements are met, and the adding amount of permanganate, chlorine dioxide and sodium hypochlorite is kept;
when the chlorine dioxide is more than or equal to 0.3mg/L, the adding amount of the chlorine dioxide is automatically reduced; when the iron is more than or equal to 0.3mg/L, the adding amount of chlorine dioxide is correspondingly and automatically reduced in proportion, and when the manganese is more than or equal to 0.2mg/L, the adding amount of permanganate is automatically reduced, and the combined adding central control module is used for intelligent analysis and control in the whole process.
Preferably, after the pollution degree of the water source water is gradually reduced, the central integrated control module automatically analyzes according to the adding amount of permanganate, chlorine dioxide and sodium hypochlorite: if after the long-time composite ring feeding adjustment control of the central integrated artificial intelligence system, the unit consumption of the permanganate water feeding amount per kiloton is lower than 0.3KG, the central integrated artificial intelligence system automatically stops the permanganate feeding subsystem according to a preset algorithm and automatically switches to a chlorine dioxide and sodium hypochlorite double-element feeding state, so that the waste is reduced, and the feeding cost is reduced.
The beneficial effects of the invention are as follows:
1. the combined type technical method is adopted, three subsystems of chlorine dioxide-sodium hypochlorite-permanganate are integrated into a combined feeding central control module, various combined feeding technical schemes are adopted for different situations of iron and manganese pollution indexes of source water, different feeding positions, different feeding sequences and different feeding amounts are accurately adjusted at the same time, and the effects of removing different pollution indexes, reducing byproducts and ensuring that the effluent stably reaches the standard are achieved.
2. The aim of deeply removing the iron and manganese indexes is achieved by starting a chlorine dioxide dosing subsystem, the aim of continuously disinfecting filtered water is achieved by starting a sodium hypochlorite dosing subsystem, further, through combined operation, when source water is heavily polluted by the iron and manganese indexes, the former two processes ensure that chlorite byproducts which are not excessively derived by the iron and manganese indexes are removed through pre-oxidation, the last process does not derive excessive chlorate byproducts, and the key indexes of chlorate of leaving water are controlled to be less than 0.7mg/L, chlorite less than 0.7mg/L, turbidity less than 1NTU, chroma less than 15 degrees, 0.1mg/L and residual chlorine dioxide less than 0.8mg/L through combined processes, so that the effect of exceeding the risk of other indexes of drinking water is ensured to be avoided.
3. Through adding three sets of systems of the sub-system with potassium permanganate throwing sub-system, chlorine dioxide throwing sub-system, sodium hypochlorite throwing sub-system and effectively superposing, control through the integrated artificial intelligence system of central authorities, can realize accurate, automatic, unmanned on duty and throw, whole dosing system is controllable, each item parameter index is readable, the operation process is controllable, the real operation process is succinct convenient, water supply industry can in time open the reply when emergent real operation.
4. By adopting a combined technical method, corresponding subsystems can be timely and selectively started according to different pollution degrees of iron and manganese in raw water, the operation parameters of each subsystem are dynamically adjusted through feedback information of water quality indexes in the treatment process, the operation working conditions of pre-oxidation and disinfection are selected to the maximum extent, mutual interference and mutual influence between pre-oxidation and disinfection are avoided, and therefore the effects of effectively removing the iron and manganese indexes, ensuring the surplus of the disinfectant in the factory water and reducing and controlling the concentration of derived byproducts are achieved.
Drawings
FIG. 1 is a schematic diagram of a combined treatment method for water pollution treatment according to the present invention;
FIG. 2 is a block diagram of a centralized artificial intelligence system for a combined treatment method for water pollution treatment according to the present invention;
FIG. 3 is a block diagram of a chlorine dioxide dosing subsystem of the combined treatment method for water pollution treatment according to the present invention;
FIG. 4 is a block diagram of a sodium hypochlorite adding subsystem of the combined treatment method for water pollution treatment provided by the invention;
FIG. 5 is a block diagram of a permanganate addition subsystem of the combined treatment process for water pollution treatment according to the present invention;
FIG. 6 is a block diagram of a sodium hypochlorite and permanganate precise addition control module of the combined treatment method for water pollution treatment provided by the invention;
FIG. 7 is a block diagram of a chlorine dioxide and sodium hypochlorite accurate feeding control module of the combined treatment method for water pollution treatment provided by the invention;
FIG. 8 is a block diagram of a combined dosing central control module of the combined technology treatment method for water pollution treatment provided by the invention.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments.
Referring to fig. 1-8, a combined technical treatment method for water pollution treatment comprises a central integrated artificial intelligence system, a chlorine dioxide dosing subsystem, a sodium hypochlorite dosing subsystem and a permanganate dosing subsystem, wherein the central integrated artificial intelligence system performs intelligent control management on the chlorine dioxide dosing subsystem, the sodium hypochlorite dosing subsystem and the permanganate dosing subsystem.
The system also comprises a first step that the central integrated artificial intelligence system comprises an online information acquisition module, an information collecting visual interface module, an accurate feeding control module, a combined feeding central control module, a safety early warning protection module and an automatic report generation module.
And step two, collecting turbidity values, residual chlorine values, pH values, residual chlorine dioxide values and alarm instrument data in the working process of the chlorine dioxide adding subsystem, the sodium hypochlorite adding subsystem and the permanganate adding subsystem through an online information collecting module, and displaying the data collected by the online information collecting module through an information summarizing visual interface module.
And thirdly, performing accurate adding control on a chlorine dioxide adding subsystem, a sodium hypochlorite adding subsystem and a permanganate adding subsystem through an accurate adding control module, wherein the online data given standard value of chlorine dioxide in filtered water is 0.3mg/L, when the system detects that the online residual chlorine dioxide value is 0.33mg/L, the system feeds back the data to the accurate adding control module, the accurate adding control module analyzes that the value is higher than the given value by 10 percent, an adjusting mechanism is triggered, the accurate adding control module sends out an instruction for reducing the frequency of a first digital metering pump by 10 percent, the frequency of the first digital metering pump is automatically adjusted down in real time according to the down-adjusting range after the first digital metering pump receives the down-adjusting instruction, the operation for adjusting the 10 percent adding amount is completed, the process of manual intelligent automatic adjustment is realized, the combined adding central control module is matched with the chlorine dioxide adding subsystem, the sodium hypochlorite added by the sodium hypochlorite adding subsystem and the real-time adding condition of the permanganate added by the permanganate adding subsystem, and the combined adding central control module is matched with the accurate adding control module, and the real-time adding amount of the chlorine dioxide, the sodium hypochlorite and the permanganate adding.
The maximum function of the combined feeding central control module is to integrate the chlorine dioxide feeding subsystem, the sodium hypochlorite feeding subsystem and the permanganate feeding subsystem through a set of preset artificial intelligence algorithm, so that the subsystems can run independently and run in a combined mode, the advantages of the subsystems can be achieved, the performance which cannot be achieved by the subsystems after combination can be achieved, the central integrated control module is combined into the combined feeding system through the integrated subsystems, the functions which cannot be achieved by the subsystems are fully excavated, and the purpose of effective, safe, stable and intelligent treatment and disposal under the condition of heavy pollution of water source water is achieved.
The automatic report generation module can collect information such as alarm information and important operation parameters generated in the operation process of the system, form a new form of report and a form for storage, and provide operation personnel for inquiring, analyzing and comparing historical data curves, thereby providing a data analysis basis for production management.
The chlorine dioxide dosing subsystem comprises a chlorine dioxide generator, a first digital metering pump, a first intelligent control system, a first raw material storage tank and a first chlorine leakage alarm instrument, wherein the type of the chlorine dioxide generator is that the effective chlorine yield is 20kg/h, N =9.0kW, the size is 1160 multiplied by 700 multiplied by 1970mm, the brand is Shanda Huate, the type of the first digital metering pump is DLTA0450, 49L/h,4bar and 78w, the brand is German ordinary Luo Mingte, the brand of the first intelligent control system is that a PLC adopts AB MICRO LOGIX 1000 series, a touch screen adopts 10-inch Kuntze-Tong, an electrical element adopts German Siemens, the volume of the first raw material storage tank is 30 cubic, the brand is Alibei, the chlorine dioxide generator respectively stores liquid hydrochloric acid and liquid sodium chlorate in the first raw material storage tank, the first digital metering pump accurately meters the hydrochloric acid and the sodium chlorate and then delivers the hydrochloric acid and the sodium chlorate to a reaction kettle of the chlorine dioxide generator, the chlorine dioxide generator heats the chlorine dioxide generator to generate a mixed gas after the mixed gas, and the chlorine dioxide generator is delivered to a water flow generator and is delivered to a water flow mixing and a water flow generator.
The first intelligent control system controls the adding amount of the hydrochloric acid and the sodium chlorate by adjusting the operating frequency of the first digital metering pump, the first chlorine leakage alarm instrument timely feeds back the chlorine dioxide gas leakage monitoring result to the central integrated artificial intelligent system when monitoring the leakage of the chlorine dioxide gas, and the central integrated artificial intelligent system reminds operators on duty to take emergency measures by sound-light alarm and carries out shutdown or pressure reduction protection measures on the chlorine dioxide adding subsystem.
The sodium hypochlorite dosing subsystem comprises a second digital metering pump, a second raw material storage tank, a second intelligent control system, a second chlorine leakage alarm instrument and an emergency recovery device, the model of the second digital metering pump is GB1200, the flow is 1200L/h, the pressure is 3.5Bar, the motor power is 0.75KW, the brand is Mi Duluo, the PLC brand of the second intelligent control system is AB, the brand of the touch screen is Tongtai, the brand of the electrical component is German Siemens, the models of the first chlorine leakage alarm instrument and the second chlorine leakage alarm instrument are SBD-100D, the two probes are arranged, the probe is 1-5ppm, the brand is Beijing Tonghun, the sodium hypochlorite is diluted to 5% concentration by purchasing a 10% sodium hypochlorite solution meeting the national standard requirement on the market, and then is used, and the second raw material storage tank stores the sodium hypochlorite solution diluted to 5% concentration.
Through the second intelligent control system, the adding amount of the sodium hypochlorite is accurately added by controlling the operating frequency of the second digital metering pump, when the second chlorine leakage alarm instrument monitors sodium hypochlorite leakage, the sodium hypochlorite leakage is timely fed back to the central integrated artificial intelligence system, the central integrated artificial intelligence system reminds an operator on duty to take emergency measures through sound-light alarm, and the sodium hypochlorite adding subsystem is controlled to stop running, an automatic protection device is triggered, when the leakage of the large area of the sodium hypochlorite occurs, the leaked sodium hypochlorite flows into a recovery tank through a gravity flow mode to be safely recovered.
The permanganate adding subsystem comprises a third digital metering pump, a third raw material storage tank, a permanganate leakage monitoring and treating module and a third intelligent control system, the model of the third digital metering pump is GB1800, the flow is 1800L/h, the pressure is 3.5Bar, the motor power is 1.25KW, the brand is Mi Duluo, the volume of the third raw material storage tank is 10 cubic meters, the brand is Alibei, the PLC brand of the third intelligent control system is AB, the brand of the touch screen is Siemens, the brand of the electrical element is Siemens, permanganate is obtained by directly purchasing a 3% concentration permanganate solution on the market, and the third raw material storage tank stores the 3% concentration permanganate solution.
The permanganate adding amount is accurately added by controlling the operating frequency of a third digital metering pump through a third intelligent control system, when the permanganate leakage monitoring and disposing module monitors that the permanganate leaks, the permanganate leakage monitoring and disposing module feeds back the permanganate leakage monitoring and disposing module to a central integrated artificial intelligent system in time, the central integrated artificial intelligent system reminds operators on duty to take emergency measures through sound-light alarm, controls a permanganate adding subsystem to stop operating, and triggers an automatic protection device.
In the process of executing the first step to the third step, when the water quality online instrument detects that the iron index concentration of raw water is between 0.2mg/L and 0.4mg/L and the manganese index concentration is between 0.1mg/L and 0.2mg/L, the central integrated artificial intelligence system analyzes source water to obtain that the source water is slightly polluted, the central integrated artificial intelligence system sends an instruction to control the chlorine dioxide adding subsystem to operate independently, the adding point is preset to be the front filtering end and the rear filtering end, 1.0-2.0 mg/L of chlorine dioxide is added to the front filtering end in the first step, 2.0-1.0 mg/L of chlorine dioxide is added to the rear filtering end in the second step, and the total adding amount before and after filtering is controlled to be less than or equal to 3mg/L.
After chlorine dioxide adding operation is executed, the central integrated artificial intelligence system judges and analyzes the collected filtered water on-line chlorine dioxide, on-line turbidity, on-line manganese index and on-line iron index values, and the standards of the filtered water on the chlorine dioxide, turbidity, iron and manganese index values are as follows: chlorine dioxide is less than or equal to 0.1mg/L, turbidity is between 0.3 and 0.6NTU, iron is between 0.1 and 0.2mg/L, and manganese is between 0.05 and 0.1mg/L.
When the index values of chlorine dioxide, turbidity, iron and manganese in the filtered water all accord with preset values, the central integrated artificial intelligence system controls the chlorine dioxide adding subsystem to execute the current operation to form a composite loop period without changing the adding point and adding amount of the chlorine dioxide.
When the index values of chlorine dioxide, turbidity, iron and manganese of the filtered water deviate from the preset requirements, the chlorine dioxide adding subsystem recognizes that the adding amount is insufficient, sends an up-regulation instruction to the first digital metering pump, and up-regulates the frequency of the first digital metering pump in a certain proportion through a preset algorithm to realize that the index of the filtered water reaches the standard.
The water quality indexes after the adjustment of the compound ring period of the chlorine dioxide adding subsystem are respectively that the chlorine dioxide is less than or equal to 0.1mg/L, the turbidity is between 0.6 and 1.0NTU, the iron is between 0.2 and 0.3mg/L and the manganese is between 0.1 and 0.2mg/L, which indicates that the iron and manganese pollution degree of raw water is increased.
Entering next-step upgrading management and control operation, analyzing source water by a combined feeding central control module to obtain that the source water is moderately polluted, adaptively and synchronously starting a sodium hypochlorite feeding subsystem by the combined feeding artificial intelligence module, synchronously stopping feeding of chlorine dioxide at the rear end of the filter, automatically switching a feeding point to be fed to the front end of the filter by the central integrated artificial intelligence system, feeding the chlorine dioxide at the rear end of the filter, and firstly feeding the chlorine dioxide at the front end of the filter, wherein the feeding amount is controlled to be 2.9-3.8 mg/L; and secondly, adding sodium hypochlorite at the rear end of the filter, wherein the adding amount is controlled to be 2.2-1.8 mg/L.
The central integrated artificial intelligence system is used for acquiring the index values of chlorine dioxide, turbidity, iron and manganese of the filtered water according to the real-time acquisition: residual chlorine is less than or equal to 0.1mg/L, turbidity is between 0.3 and 0.6NTU, iron is between 0.1 and 0.2mg/L, manganese is between 0.05 and 0.1mg/L, the central integrated artificial intelligence system recognizes that the adding amount is insufficient, an up-regulation instruction is sent to the first digital metering pump and the second digital metering pump, the frequency of chlorine dioxide and sodium hypochlorite metering pumps is regulated up in a certain proportion through a preset algorithm, and the index of the filtered water reaches the standard.
The water quality indexes after the addition period adjustment of the chlorine dioxide addition subsystem and the sodium hypochlorite addition subsystem are respectively that the chlorine dioxide is less than or equal to 0.1mg/L, the turbidity is between 0.6 and 1.0NTU, the iron is between 0.2 and 0.3mg/L and the manganese is between 0.1 and 0.2mg/L, which indicates that the iron and manganese pollution degree of raw water is further increased.
Continuing to upgrade the management and control operation in the next step, analyzing the water quality index of the source water by the central integrated artificial intelligence system, identifying that the identification result is severe pollution, and showing that the problem can not be solved by the matching scheme of the chlorine dioxide dosing subsystem and the sodium hypochlorite dosing subsystem controlled by the combined dosing central control module, starting the permanganate dosing subsystem by adaptively increasing the combined dosing central control module at the moment, and automatically switching the dosing point to: adding permanganate at the front end of flocculation, adding chlorine dioxide at the front end of filtration, and adding sodium hypochlorite at the rear end of filtration, wherein in the first step, the permanganate is added at the front end of flocculation, and the adding amount is controlled to be 0.5-3.0 mg/L; secondly, adding chlorine dioxide at the front end of the filter, wherein the total adding amount is controlled to be less than or equal to 3.0mg/L; thirdly, adding sodium hypochlorite at the rear end of the filter, wherein the total adding amount is controlled to be less than or equal to 2.5mg/L.
The central integrated artificial intelligence system carries out comprehensive analysis and dynamic adjustment according to the index values of the filtered water chlorine dioxide, turbidity, iron and manganese collected in real time: if the chlorine dioxide in the filtered water index is less than or equal to 0.1mg/L, the turbidity is between 0.1 and 0.2NTU, the iron is between 0.05 and 0.1mg/L, and the manganese is between 0.02 and 0.05mg/L, the preset requirements are met, and the adding amount of permanganate, chlorine dioxide and sodium hypochlorite is kept.
When the chlorine dioxide is more than or equal to 0.3mg/L, the adding amount of the chlorine dioxide is automatically reduced; when the iron is more than or equal to 0.3mg/L, the adding amount of chlorine dioxide is correspondingly and automatically reduced in proportion, and when the manganese is more than or equal to 0.2mg/L, the adding amount of permanganate is automatically reduced, and a combined adding central control module is used for intelligent analysis and control in the whole process.
After the water pollution degree of the water source is reduced step by step, the central integrated control module performs automatic analysis according to the adding amount of permanganate, chlorine dioxide and sodium hypochlorite: if the unit consumption of the permanganate water dosage per kiloton is lower than 0.3KG after the long-time compound ring dosing adjustment control of the central integrated artificial intelligence system, the central integrated artificial intelligence system automatically stops the permanganate dosing subsystem according to a preset algorithm and automatically switches to a chlorine dioxide and sodium hypochlorite double-element dosing state, waste is reduced, and dosing cost is reduced.
The system can manually input the adding parameters under the condition of manual intervention, the central integrated artificial intelligence system can intelligently add according to the given parameters, and the function can realize full-automatic and intelligent combined adding control under the condition of lacking on-line instrument data feedback on site.
The above description is only for the preferred embodiment of the present invention, but the scope of the present invention is not limited thereto, and any person skilled in the art should be considered to be within the technical scope of the present invention, and the technical solutions and the inventive concepts thereof according to the present invention should be equivalent or changed within the scope of the present invention.

Claims (10)

1. A combined technology treatment method for water pollution treatment is characterized in that: the intelligent chlorine dioxide adding system comprises a central integrated artificial intelligence system, a chlorine dioxide adding subsystem, a sodium hypochlorite adding subsystem and a permanganate adding subsystem, wherein the central integrated artificial intelligence system is right for the chlorine dioxide adding subsystem, the sodium hypochlorite adding subsystem and the permanganate adding subsystem to carry out intelligent control management.
2. The combined technical treatment method for water pollution treatment according to claim 1, which is characterized in that:
the central integrated artificial intelligence system comprises an online information acquisition module, an information gathering visual interface module, an accurate feeding control module, a combined feeding central control module, a safety early warning protection module and an automatic report generation module;
secondly, the turbidity value, the residual chlorine value, the pH value, the residual chlorine dioxide value and the data of an alarm instrument in the working process of the chlorine dioxide adding subsystem, the sodium hypochlorite adding subsystem and the permanganate adding subsystem are collected through the online information collecting module, and the information summarizing visual interface module displays the data collected by the online information collecting module;
step three, pass through the accurate control module of throwing is right chlorine dioxide adds the subsystem into chlorine dioxide add the subsystem with the permanganate adds the subsystem and carries out the accurate control of throwing, it is right to jointly add central control module chlorine dioxide that chlorine dioxide adds the subsystem and throws sodium hypochlorite that the subsystem was thrown with the real-time condition of throwing of permanganate that the subsystem was thrown with the permanganate carries out intelligent analysis, jointly add central control module with the accurate control module of throwing is mutually supported, and intelligent control or the real-time volume of throwing of adjustment chlorine dioxide, sodium hypochlorite and permanganate.
3. The combined technical treatment method for water pollution treatment according to claim 2, which is characterized in that: the chlorine dioxide dosing subsystem comprises a chlorine dioxide generator, a first digital metering pump, a first intelligent control system, a first raw material storage tank and a first chlorine leakage alarm instrument, wherein the chlorine dioxide generator respectively stores liquid hydrochloric acid and liquid sodium chlorate in the first raw material storage tank.
4. The combined technology treatment method for water pollution treatment according to claim 3, characterized in that: the first digital metering pump accurately meters the hydrochloric acid and the sodium chlorate and then conveys the hydrochloric acid and the sodium chlorate to a reaction kettle of a chlorine dioxide generator, the chlorine dioxide generator heats the hydrochloric acid and the sodium chlorate through a water bath to mix the hydrochloric acid and the sodium chlorate to generate chlorine dioxide gas, and the chlorine dioxide gas overflowing from the reaction kettle of the chlorine dioxide generator is carried by negative pressure generated by a water injector in the chlorine dioxide generator, is mixed with water flow and is conveyed to a feeding point of a chlorine dioxide feeding subsystem;
the first intelligent control system controls the adding amount of hydrochloric acid and sodium chlorate by adjusting the operating frequency of the first digital metering pump, the first chlorine leakage alarm instrument timely feeds back to the central integrated artificial intelligent system when monitoring the leakage of chlorine dioxide gas, and the central integrated artificial intelligent system reminds operators on duty to take emergency measures by sound-light alarm and carries out shutdown or pressure reduction protection measures on the chlorine dioxide adding subsystem.
5. The combined technical treatment method for water pollution treatment according to claim 4, which is characterized in that: the sodium hypochlorite adding subsystem comprises a second digital metering pump, a second raw material storage tank, a second intelligent control system, a second chlorine leakage alarm instrument and an emergency recovery device, and the second raw material storage tank stores a sodium hypochlorite solution diluted to 5% in concentration;
through second intelligence control system is through control the operating frequency of second digital measuring pump carries out the accuracy to sodium hypochlorite's the volume of throwing with throwing, when the second leaks the chlorine alarm appearance and monitors sodium hypochlorite and leak, in time feed back to integrated artificial intelligence system of central authorities, integrated artificial intelligence system of central authorities reminds the person on duty to take emergency measures through audible-visual alarm, and control sodium hypochlorite dosing subsystem stall, trigger automatic safety device, emergent recovery unit makes the sodium hypochlorite of leaking flow into the recovery pond through the mode that gravity flowed and carries out the safety recovery when sodium hypochlorite takes place to leak by a large scale.
6. The combined technical treatment method for water pollution treatment according to claim 5, which is characterized in that: the permanganate adding subsystem comprises a third digital metering pump, a third raw material storage tank, a permanganate leakage monitoring and treating module and a third intelligent control system, wherein the third raw material storage tank stores a 3% permanganate solution;
through third intelligence control system is through control the operating frequency of third digital metering pump carries out the accuracy to the volume of throwing of permanganate and throws, when permanganate leakage is monitored and is dealt with the module and monitor the permanganate and leak, in time feed back to central integrated artificial intelligence system, central integrated artificial intelligence system reminds the person on duty to take emergency measures through audible and visual alarm, and control permanganate throwing subsystem stop operation triggers automatic safety device.
7. The combined technical treatment method for water pollution treatment according to claim 6, which is characterized in that: in the process of executing the first step to the third step, when a water quality online instrument detects that the iron index concentration of raw water is between 0.2mg/L and 0.4mg/L and the manganese index concentration is between 0.1mg/L and 0.2mg/L, the central integrated artificial intelligence system analyzes source water to obtain that the source water is slightly polluted, the central integrated artificial intelligence system sends an instruction to control the chlorine dioxide adding subsystem to operate independently, an adding point is preset to be a front filtering end and a rear filtering end, 1.0-2.0 mg/L of chlorine dioxide is added to the front filtering end in the first step, 2.0-1.0 mg/L of chlorine dioxide is added to the rear filtering end in the second step, and the total adding amount of the chlorine dioxide before and after filtering is controlled to be less than or equal to 3mg/L;
after chlorine dioxide adding operation is executed, the central integrated artificial intelligence system judges and analyzes the values of collected filtered water on-line chlorine dioxide, on-line turbidity, on-line manganese indexes and on-line iron indexes, and the standards of the values of the filtered water on the chlorine dioxide, turbidity, iron and manganese indexes are as follows: chlorine dioxide is less than or equal to 0.1mg/L, turbidity is between 0.3 and 0.6NTU, iron is between 0.1 and 0.2mg/L, and manganese is between 0.05 and 0.1mg/L;
when the index values of chlorine dioxide, turbidity, iron and manganese in the filtered water all accord with preset values, the central integrated artificial intelligence system controls a chlorine dioxide adding subsystem to execute the current operation to form a composite ring period without changing the adding point and adding amount of the chlorine dioxide;
when the index values of chlorine dioxide, turbidity, iron and manganese of the filtered water deviate from the preset requirements, the chlorine dioxide adding subsystem recognizes that the adding amount is insufficient, and sends an up-regulation instruction to the first digital metering pump.
8. The combined technical treatment method for water pollution treatment according to claim 7, which is characterized in that: the water quality indexes after the composite ring period adjustment of the chlorine dioxide adding subsystem are respectively that the chlorine dioxide is less than or equal to 0.1mg/L, the turbidity is between 0.6 and 1.0NTU, the iron is between 0.2 and 0.3mg/L and the manganese is between 0.1 and 0.2mg/L, which indicates that the iron and manganese pollution degree of raw water is increased;
entering next-step upgrading management and control operation, analyzing the source water by the combined feeding central control module to obtain that the source water is moderately polluted, starting the sodium hypochlorite feeding subsystem in a self-adaptive and synchronous mode by the combined feeding artificial intelligence module, stopping feeding of chlorine dioxide at the rear end of the filter synchronously, automatically switching a feeding point to be the feeding of the chlorine dioxide at the front end of the filter by the central integrated artificial intelligence system, feeding the chlorine dioxide at the rear end of the filter by the central integrated artificial intelligence system, and firstly feeding the chlorine dioxide at the front end of the filter, wherein the feeding amount is controlled to be 2.9 mg/L-3.8 mg/L; secondly, adding sodium hypochlorite at the rear end of the filter, wherein the adding amount is controlled to be 2.2-1.8 mg/L;
the central integrated artificial intelligence system is used for collecting the index values of chlorine dioxide, turbidity, iron and manganese of the filtered water in real time: residual chlorine is less than or equal to 0.1mg/L, turbidity is between 0.3 and 0.6NTU, iron is between 0.1 and 0.2mg/L, manganese is between 0.05 and 0.1mg/L, and an up-regulation instruction is sent to a second digital metering pump when the sodium hypochlorite feeding subsystem recognizes that the feeding amount is insufficient.
9. The combined technical treatment method for water pollution treatment according to claim 8, wherein the combined technical treatment method comprises the following steps: the water quality indexes after the period adjustment of the compound ring added by the chlorine dioxide adding subsystem and the sodium hypochlorite adding subsystem are respectively that the chlorine dioxide is less than or equal to 0.1mg/L, the turbidity is between 0.6 and 1.0NTU, the iron is between 0.2 and 0.3mg/L and the manganese is between 0.1 and 0.2mg/L, which indicates that the iron and manganese pollution degree of raw water is further increased;
continuing upgrading the management and control operation next step, the integrated artificial intelligence system of central authorities analyzes source water quality index, and the recognition result is heavily polluted, explains through jointly throw chlorine dioxide dosing subsystem and sodium hypochlorite dosing subsystem cooperation scheme that adds central control module control and can't solve the problem, at this moment jointly throw with central control module with the self-adaptation increase start permanganate dosing subsystem, throw the some automatic switch and become: adding permanganate at the front end of flocculation, adding chlorine dioxide at the front end of filtration, and adding sodium hypochlorite at the rear end of filtration, wherein in the first step, the permanganate is added at the front end of flocculation, and the adding amount is controlled to be 0.5-3.0 mg/L; secondly, adding chlorine dioxide at the front end of the filter, wherein the total adding amount is controlled to be less than or equal to 3.0mg/L; thirdly, adding sodium hypochlorite at the rear end of the filter, wherein the total adding amount is controlled to be less than or equal to 2.5mg/L;
the central integrated artificial intelligence system carries out comprehensive analysis and dynamic adjustment according to the index values of filtered water chlorine dioxide, turbidity, iron and manganese collected in real time: if the chlorine dioxide in the filtered water index is less than or equal to 0.1mg/L, the turbidity is between 0.1 and 0.2NTU, the iron is between 0.05 and 0.1mg/L, the manganese is between 0.02 and 0.05mg/L, the preset requirements are met, and the adding amount of permanganate, chlorine dioxide and sodium hypochlorite is kept;
when the chlorine dioxide is more than or equal to 0.3mg/L, the adding amount of the chlorine dioxide is automatically reduced; when the iron is more than or equal to 0.3mg/L, the adding amount of chlorine dioxide is correspondingly and automatically reduced in proportion, and when the manganese is more than or equal to 0.2mg/L, the adding amount of permanganate is automatically reduced, and the combined adding central control module is used for intelligent analysis and control in the whole process.
10. The combined technical treatment method for water pollution treatment according to claim 9, which is characterized in that: after the water pollution degree of the water source is reduced step by step, the central integrated control module performs automatic analysis according to the adding amount of permanganate, chlorine dioxide and sodium hypochlorite: if pass through after the long-time compound ring of integrated artificial intelligence system of central authorities throws addition adjustment control, the kiloton water of permanganate is thrown addition volume unit and is consumed when being less than 0.3KG, integrated artificial intelligence system of central authorities will be according to predetermineeing the algorithm, and the automatic shutdown permanganate throws addition subsystem to automatic switch over chlorine dioxide and sodium hypochlorite double-element throwing state, reduce the waste, reduce and throw the cost, when chlorine dioxide and sodium hypochlorite are thrown when compound ring control system under the state discerns that the kiloton water of sodium hypochlorite is thrown addition volume unit and is consumed and be less than 0.6KG, integrated artificial intelligence system of central authorities stops sodium hypochlorite throwing subsystem automatically to the conventional mode of chlorine dioxide throwing subsystem is thrown in the automatic switch, thereby further reduce the unit consumption.
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Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1103628A (en) * 1993-12-11 1995-06-14 李圭白 Drinking water purifying technique with compound permanganate medicament
CN101264997A (en) * 2008-04-17 2008-09-17 北京水气蓝德环保科技有限公司 Method for processing film filtration concentrated solution of domestic refuse percolate treatment
JP2010036180A (en) * 2008-08-07 2010-02-18 Uerushii:Kk Water treatment method
CN102583810A (en) * 2011-01-10 2012-07-18 中国科学院生态环境研究中心 Method for removing arsenic by using Fe (II) and Mn (II) in underground water
CN107628703A (en) * 2017-09-27 2018-01-26 中山大学 It is a kind of to remove the water process preoxidation technique that ferrimanganic pollutes in water removal
CN108423741A (en) * 2018-04-20 2018-08-21 东莞市顶盛环保科技有限公司 A kind of COD removers and preparation method thereof
CN110590009A (en) * 2019-09-03 2019-12-20 山东山大华特科技股份有限公司 Intelligent cooperative disinfection method suitable for complex surface water treatment
CN110885145A (en) * 2018-09-11 2020-03-17 华中科技大学 Method for synchronously removing pollutants in water body and controlling generation of bromine-containing byproducts
KR102311904B1 (en) * 2021-04-01 2021-10-13 주식회사 프로솔 a soluble manganese treatment method using the permanganate and the water treatment system using thereof
CN215559752U (en) * 2021-10-09 2022-01-18 晋江市华天市政工程有限公司 Energy-saving environment-friendly water purifying device for tap water plant

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1103628A (en) * 1993-12-11 1995-06-14 李圭白 Drinking water purifying technique with compound permanganate medicament
CN101264997A (en) * 2008-04-17 2008-09-17 北京水气蓝德环保科技有限公司 Method for processing film filtration concentrated solution of domestic refuse percolate treatment
JP2010036180A (en) * 2008-08-07 2010-02-18 Uerushii:Kk Water treatment method
CN102583810A (en) * 2011-01-10 2012-07-18 中国科学院生态环境研究中心 Method for removing arsenic by using Fe (II) and Mn (II) in underground water
CN107628703A (en) * 2017-09-27 2018-01-26 中山大学 It is a kind of to remove the water process preoxidation technique that ferrimanganic pollutes in water removal
CN108423741A (en) * 2018-04-20 2018-08-21 东莞市顶盛环保科技有限公司 A kind of COD removers and preparation method thereof
CN110885145A (en) * 2018-09-11 2020-03-17 华中科技大学 Method for synchronously removing pollutants in water body and controlling generation of bromine-containing byproducts
CN110590009A (en) * 2019-09-03 2019-12-20 山东山大华特科技股份有限公司 Intelligent cooperative disinfection method suitable for complex surface water treatment
KR102311904B1 (en) * 2021-04-01 2021-10-13 주식회사 프로솔 a soluble manganese treatment method using the permanganate and the water treatment system using thereof
CN215559752U (en) * 2021-10-09 2022-01-18 晋江市华天市政工程有限公司 Energy-saving environment-friendly water purifying device for tap water plant

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘伟强;: "二氧化氯与次氯酸钠联用降低亚氯酸盐生成量的实践研究", 海峡科学, no. 05 *
戴仲怡;: "高锰酸钾、二氧化氯及次氯酸钠组合工艺在水厂中的应用", 中国水运(下半月), no. 08 *

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