CN117819637A - Water quality information processing method and system - Google Patents
Water quality information processing method and system Download PDFInfo
- Publication number
- CN117819637A CN117819637A CN202410200850.XA CN202410200850A CN117819637A CN 117819637 A CN117819637 A CN 117819637A CN 202410200850 A CN202410200850 A CN 202410200850A CN 117819637 A CN117819637 A CN 117819637A
- Authority
- CN
- China
- Prior art keywords
- water quality
- sewage
- quality data
- nano material
- real
- 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.)
- Pending
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 169
- 230000010365 information processing Effects 0.000 title claims abstract description 19
- 238000003672 processing method Methods 0.000 title claims abstract description 14
- 239000002086 nanomaterial Substances 0.000 claims abstract description 115
- 239000010865 sewage Substances 0.000 claims abstract description 88
- 238000000034 method Methods 0.000 claims abstract description 42
- 239000000126 substance Substances 0.000 claims description 18
- 239000000376 reactant Substances 0.000 claims description 12
- 239000011343 solid material Substances 0.000 claims description 11
- 238000003860 storage Methods 0.000 claims description 11
- 238000012544 monitoring process Methods 0.000 claims description 8
- 238000002360 preparation method Methods 0.000 claims description 5
- 230000001376 precipitating effect Effects 0.000 claims description 4
- 238000004590 computer program Methods 0.000 claims description 3
- 238000012545 processing Methods 0.000 claims description 3
- 230000008569 process Effects 0.000 abstract description 8
- 239000003344 environmental pollutant Substances 0.000 abstract description 4
- 231100000719 pollutant Toxicity 0.000 abstract description 4
- 238000001179 sorption measurement Methods 0.000 description 8
- 238000006243 chemical reaction Methods 0.000 description 5
- 230000001276 controlling effect Effects 0.000 description 5
- 238000003911 water pollution Methods 0.000 description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 238000012986 modification Methods 0.000 description 4
- 230000004048 modification Effects 0.000 description 4
- 239000001301 oxygen Substances 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- 230000008878 coupling Effects 0.000 description 3
- 238000010168 coupling process Methods 0.000 description 3
- 238000005859 coupling reaction Methods 0.000 description 3
- 238000012806 monitoring device Methods 0.000 description 3
- 239000002105 nanoparticle Substances 0.000 description 3
- 230000035484 reaction time Effects 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- 238000003980 solgel method Methods 0.000 description 3
- 239000002904 solvent Substances 0.000 description 3
- 230000006978 adaptation Effects 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 238000004891 communication Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 230000006798 recombination Effects 0.000 description 2
- 238000005215 recombination Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 238000001308 synthesis method Methods 0.000 description 2
- -1 turbidity Chemical compound 0.000 description 2
- 238000007740 vapor deposition Methods 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 238000000151 deposition Methods 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 230000006870 function Effects 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000001879 gelation Methods 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 230000006911 nucleation Effects 0.000 description 1
- 238000010899 nucleation Methods 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 238000010189 synthetic method Methods 0.000 description 1
- 238000005406 washing Methods 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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/008—Control or steering systems not provided for elsewhere in subclass C02F
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
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)
- Biological Treatment Of Waste Water (AREA)
Abstract
The invention provides a water quality information processing method and a system, wherein the method comprises the following steps: acquiring first water quality data of sewage to be treated; determining the input amount of the nano material into the sewage to be treated according to the first water quality data; acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount; and according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold. According to the scheme, sewage is treated by the nano material, so that the concentration of pollutants in water can be effectively reduced, and the treatment cost is reduced; the water quality data is monitored in real time, automatic control is realized, and convenience and accuracy of the treatment process are improved.
Description
Technical Field
The invention relates to the technical field of water pollution treatment, in particular to a water quality information processing method and system.
Background
With the rapid development of industry and agriculture, the water pollution problem is increasingly serious, and the water pollution problem forms a great threat to human life and ecological environment. Traditional water pollution treatment methods tend to be inefficient and costly. Therefore, it has become urgent to find an efficient and low-cost water pollution control method.
Disclosure of Invention
The invention provides a water quality information processing method and a water quality information processing system, which can effectively reduce the concentration of pollutants in water and reduce the treatment cost by carrying out sewage treatment by nano materials; the water quality data is monitored in real time, automatic control is realized, and convenience and accuracy of the treatment process are improved.
In order to solve the technical problems, the technical scheme of the invention is as follows:
a water quality information processing method, comprising:
acquiring first water quality data of sewage to be treated;
determining the input amount of the nano material into the sewage to be treated according to the first water quality data;
acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount;
and according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold.
Optionally, acquiring first water quality data of the sewage to be treated includes:
and acquiring at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated through water quality monitoring equipment, and taking the at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated as first water quality data of the sewage to be treated.
Optionally, determining the input amount of the nanomaterial to be input into the sewage to be treated according to the first water quality data includes:
and when the first water quality data is larger than a preset water quality standard threshold value, determining the input amount of the nano material input into the sewage to be treated according to the preset water quality standard threshold value.
Optionally, the preparation process of the nanomaterial includes:
obtaining a gaseous reactant;
reacting and precipitating the gaseous reactant to obtain an intermediate solid material;
and carrying out post-treatment on the intermediate solid material to obtain the nano material.
Optionally, acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount includes:
and acquiring at least one of physical parameters, chemical parameters and biological parameters of the sewage after the nano materials are added according to the input amount by water quality monitoring equipment, and taking the at least one of the physical parameters, the chemical parameters and the biological parameters as real-time water quality data.
Optionally, according to the real-time water quality data, adjusting the input amount of the nanomaterial and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold, including:
comparing the real-time water quality data with a preset target water quality threshold value to obtain a difference;
and adjusting the input amount of the nano material and the sewage treatment time according to the difference amount.
Optionally, the method further comprises:
and recovering the nano material in the water when the real-time water quality data is smaller than or equal to a preset target water quality threshold value.
The invention also provides a water quality information processing system, which comprises:
the acquisition module is used for acquiring first water quality data of the sewage to be treated; acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount;
the treatment module is used for determining the input amount of the nano material into the sewage to be treated according to the first water quality data; and according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold.
The present invention also provides a computing device comprising: a processor, a memory storing a computer program which, when executed by the processor, performs the method as described above.
The invention also provides a computer readable storage medium storing instructions that when executed on a computer cause the computer to perform a method as described above.
The scheme of the invention at least comprises the following beneficial effects:
the scheme of the invention obtains the first water quality data of the sewage to be treated; determining the input amount of the nano material into the sewage to be treated according to the first water quality data; acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount; according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold; the sewage treatment is carried out by utilizing the nano material, so that the concentration of pollutants in water can be effectively reduced, and the treatment cost is reduced; the water quality data is monitored in real time, automatic control is realized, and convenience and accuracy of the treatment process are improved.
Drawings
FIG. 1 is a flow chart of a water quality information processing method provided by an embodiment of the present invention;
fig. 2 is a block diagram of a water quality information processing system according to an embodiment of the present invention.
Detailed Description
Exemplary embodiments of the present invention will be described in more detail below with reference to the accompanying drawings. While exemplary embodiments of the present invention are shown in the drawings, it should be understood that the present invention may be embodied in various forms and should not be limited to the embodiments set forth herein. Rather, these embodiments are provided so that this disclosure will be thorough and complete, and will fully convey the scope of the invention to those skilled in the art.
As shown in fig. 1, an embodiment of the present invention provides a water quality information processing method, including:
step 11, obtaining first water quality data of sewage to be treated;
step 12, determining the input amount of the nano material into the sewage to be treated according to the first water quality data;
step 13, acquiring real-time water quality data of the sewage after the nano material is added according to the input amount;
and 14, adjusting the input amount of the nano material and the sewage treatment time according to the real-time water quality data until the real-time water quality data reaches a preset target water quality threshold.
In this embodiment, by acquiring first water quality data of the sewage to be treated; determining the input amount of the nano material into the sewage to be treated according to the first water quality data; acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount; according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold; the sewage treatment is carried out by utilizing the nano material, so that the concentration of pollutants in water can be effectively reduced, and the treatment cost is reduced; the water quality data is monitored in real time, automatic control is realized, and convenience and accuracy of the treatment process are improved.
In an alternative embodiment of the present invention, step 11 includes:
step 111, obtaining at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated through water quality monitoring equipment, and taking the at least one of physical parameters, chemical parameters and biological parameters as first water quality data of the sewage to be treated.
In this embodiment, among others, the water quality monitoring device includes, but is not limited to: sensors and instruments such as conductivity meter, pH meter, dissolved oxygen meter, turbidity meter, etc.; physical, chemical, biological parameters include, but are not limited to: water quality indexes such as pH value, conductivity, dissolved oxygen, turbidity, ammonia nitrogen and the like; at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated is obtained through the water quality monitoring equipment and is used as first water quality data of the sewage to be treated, so that the quality and health condition of the sewage are evaluated through the first water quality data, and the subsequent targeted determination of the input amount of the nano material is facilitated.
In an alternative embodiment of the present invention, step 12 includes:
and step 121, determining the input amount of the nano material into the sewage to be treated according to the preset water quality standard threshold when the first water quality data is larger than the preset water quality standard threshold.
In the embodiment, a preset water quality standard threshold value of a plurality of ladder ranges is set according to a preset target water quality threshold value, and the input amount of the nano material is correspondingly set according to the preset water quality standard threshold value of each ladder range; after the first water quality data is obtained, comparing the first water quality data with a plurality of preset water quality standard thresholds in a plurality of step ranges, and carrying out nano material input by taking the input amount of the nano material corresponding to the preset water quality standard threshold which is closest to and smaller than the first water quality data as a standard; by determining the input amount of the nano material in the mode, waste caused by excessive input amount of the nano material can be avoided.
In an alternative embodiment of the present invention, the preparation process of the nanomaterial includes:
obtaining a gaseous reactant;
reacting and precipitating the gaseous reactant to obtain an intermediate solid material;
and carrying out post-treatment on the intermediate solid material to obtain the nano material.
In this example, by taking a gaseous reactant; the gaseous reactants are subjected to reaction precipitation to obtain an intermediate solid material, the intermediate solid material is a nano material which is obtained preliminarily, and the intermediate solid material is subjected to post-treatment through steps of washing, centrifuging, filtering, drying and the like to remove impurities and solvents, so that the purity, dispersibility and stability of the nano material are improved, and the performance of the nano material is ensured;
the present embodiment uses vapor deposition to prepare nanomaterial, and it should be noted that nanomaterial may also be prepared by other methods including, but not limited to: a solution phase synthesis method, a sol-gel method;
when the vapor deposition method is used for preparing the nano material, the growth of the nano material is controlled by adjusting parameters such as deposition temperature, gas flow, reaction time and the like, so that the morphology of the nano material is controlled, and the adsorption performance of the nano material is ensured; when the solution phase synthesis method is used for preparing the nano material, the nucleation and growth rate in the solution are regulated and controlled by selecting different solution systems, adjusting the conditions of reaction temperature, pH value and the like, so that the morphology of the nano material is controlled; when the sol-gel method is used for preparing the nano material, the nano material is obtained by controlling the gelation process of the sol, so that the size and the morphology of the nano particles can be controlled;
when the method is used for preparing the nano material, the adsorption performance of the nano material is improved by the following method:
controlling the temperature and the pressure, and obtaining the nano material with larger specific surface area and higher adsorption capacity by adjusting the temperature and the pressure to influence the reaction rate and the properties of the product;
the reaction time and the rate are controlled, and the size and the morphology of the nano particles are controlled by precisely controlling the reaction time and the rate, so that the adsorption performance of the nano material is improved;
controlling the concentration of the reactant, influencing the generation rate and the size of the nano particles by controlling and adjusting the concentration of the reactant, and improving the adsorption capacity of the nano material;
surface modification, namely, introducing functional groups to improve the hydrophilicity or lipophilicity of the nano material by carrying out surface modification on the nano material, so as to improve the adsorption specificity and capacity;
the solvent is selected, and in the preparation process of sol-gel method and the like, the uniformity and stability of the nano material can be improved by selecting a proper solvent;
the catalyst is used, and the catalyst is introduced in some synthetic methods to accelerate the reaction rate, so that the nano material with high-efficiency adsorption performance can be prepared.
In an alternative embodiment of the present invention, step 13 includes:
step 131, obtaining by a water quality monitoring device, and taking at least one of physical parameters, chemical parameters and biological parameters of the sewage into which the nano material is put as real-time water quality data according to the input amount.
In this embodiment, among others, the water quality monitoring device includes, but is not limited to: sensors and instruments such as conductivity meter, pH meter, dissolved oxygen meter, turbidity meter, etc.; physical, chemical, biological parameters include, but are not limited to: water quality indexes such as pH value, conductivity, dissolved oxygen, turbidity, ammonia nitrogen and the like; and the sewage treatment progress is judged through the real-time water quality data, so that the subsequent adjustment of the nano material input amount and the sewage treatment time is facilitated.
In an alternative embodiment of the present invention, step 14 includes:
step 141, comparing the real-time water quality data with a preset target water quality threshold value to obtain a difference;
and step 142, adjusting the input amount of the nano material and the sewage treatment time according to the difference amount.
In the embodiment, the real-time water quality data is compared with a preset target water quality threshold value to obtain a difference quantity, and the sewage treatment process is judged according to the difference quantity, so that the input quantity of the nano material and the sewage treatment time are correspondingly adjusted; specifically, when the difference amount is large and the change is small, the input amount of the nano material is increased, and the sewage treatment time is increased; when the difference is steadily and gradually reduced, the input amount of the nano material and the sewage treatment time are not adjusted; when the difference amount is rapidly reduced, the input amount of the nano material is reduced, and the sewage treatment time is shortened; by adjusting the input amount of the nano material and the sewage treatment time according to the difference amount, the overall treatment efficiency is improved while the sewage treatment effect is ensured, and the nano material is reasonably and properly used, so that the waste of the nano material is avoided.
In an optional embodiment of the present invention, the method further includes:
and recovering the nano material in the water when the real-time water quality data is smaller than or equal to a preset target water quality threshold value.
In the embodiment, when the real-time water quality data is smaller than or equal to the preset target water quality threshold value, the nano materials in the water are recovered, and the nano materials are recycled, so that the sewage treatment cost can be reduced;
the recovery method of the nano material comprises the following steps:
when the density difference between the nano material and the solution is large, the centrifugal separation method utilizes the density difference between the nano material and the solution to separate by a centrifugal machine;
a precipitation method in which the nanomaterial is precipitated by adding a precipitant to a solution when the nanomaterial exists in a dissolved state in the solution, and then separated;
the adsorption method comprises the steps that when the nano material exists in a colloid or suspension state in a solution, the nano material is adsorbed by an adsorbent, and then the nano material is desorbed from the adsorbent by methods such as elution or heating;
extraction method: when the nano material exists in a solution in a dissolved or colloidal state, the separation and recovery of the nano material are realized by utilizing the solute distribution principle and chemical reaction characteristics between two immiscible liquids;
and (3) magnetic recovery, wherein when the nanomaterial is magnetic, the magnet is utilized to adsorb the nanomaterial, so that the nanomaterial is recovered.
As shown in fig. 2, an embodiment of the present invention further provides a water quality information processing system 20, including:
an acquisition module 21 for acquiring first water quality data of the sewage to be treated; acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount;
a processing module 22, configured to determine an input amount of the nanomaterial to be input into the sewage to be processed according to the first water quality data; and according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold.
Optionally, acquiring first water quality data of the sewage to be treated includes:
and acquiring at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated through water quality monitoring equipment, and taking the at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated as first water quality data of the sewage to be treated.
Optionally, determining the input amount of the nanomaterial to be input into the sewage to be treated according to the first water quality data includes:
and when the first water quality data is larger than a preset water quality standard threshold value, determining the input amount of the nano material input into the sewage to be treated according to the preset water quality standard threshold value.
Optionally, the preparation process of the nanomaterial includes:
obtaining a gaseous reactant;
reacting and precipitating the gaseous reactant to obtain an intermediate solid material;
and carrying out post-treatment on the intermediate solid material to obtain the nano material.
Optionally, acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount includes:
and acquiring at least one of physical parameters, chemical parameters and biological parameters of the sewage after the nano materials are added according to the input amount by water quality monitoring equipment, and taking the at least one of the physical parameters, the chemical parameters and the biological parameters as real-time water quality data.
Optionally, according to the real-time water quality data, adjusting the input amount of the nanomaterial and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold, including:
comparing the real-time water quality data with a preset target water quality threshold value to obtain a difference;
and adjusting the input amount of the nano material and the sewage treatment time according to the difference amount.
Optionally, the method further comprises:
and recovering the nano material in the water when the real-time water quality data is smaller than or equal to a preset target water quality threshold value.
It should be noted that, the system is a system corresponding to the above method, and all implementation manners in the above method embodiments are applicable to the system embodiment, so that the same technical effects can be achieved.
There is also provided, in an embodiment of the present invention, a computing device including: a processor, a memory storing a computer program which, when executed by the processor, performs the method as described in the above embodiments. All the implementation manners in the method embodiment are applicable to the embodiment, and the same technical effect can be achieved.
Embodiments of the present invention also provide a computer readable storage medium storing instructions that, when executed on a computer, cause the computer to perform a method as described in the above embodiments. All the implementation manners in the method embodiment are applicable to the embodiment, and the same technical effect can be achieved.
Those of ordinary skill in the art will appreciate that the various illustrative elements and algorithm steps described in connection with the embodiments disclosed herein may be implemented as electronic hardware, or combinations of computer software and electronic hardware. Whether such functionality is implemented as hardware or software depends upon the particular application and design constraints imposed on the solution. Skilled artisans may implement the described functionality in varying ways for each particular application, but such implementation decisions should not be interpreted as causing a departure from the scope of the present invention.
It will be clear to those skilled in the art that, for convenience and brevity of description, specific working procedures of the above-described systems, apparatuses and units may refer to corresponding procedures in the foregoing method embodiments, and are not repeated herein.
In the embodiments provided in the present invention, it should be understood that the disclosed system and method may be implemented in other manners. For example, the system embodiments described above are merely illustrative, e.g., the division of the elements is merely a logical functional division, and there may be additional divisions when actually implemented, e.g., multiple elements or components may be combined or integrated into another system, or some features may be omitted or not performed. Alternatively, the coupling or direct coupling or communication connection shown or discussed with each other may be an indirect coupling or communication connection via some interfaces, devices or units, which may be in electrical, mechanical or other form.
The units described as separate units may or may not be physically separate, and units shown as units may or may not be physical units, may be located in one place, or may be distributed on a plurality of network units. Some or all of the units may be selected according to actual needs to achieve the purpose of the solution of this embodiment.
In addition, each functional unit in the embodiments of the present invention may be integrated in one processing unit, or each unit may exist alone physically, or two or more units may be integrated in one unit.
The functions, if implemented in the form of software functional units and sold or used as a stand-alone product, may be stored in a computer-readable storage medium. Based on this understanding, the technical solution of the present invention may be embodied essentially or in a part contributing to the prior art or in a part of the technical solution, in the form of a software product stored in a storage medium, comprising several instructions for causing a computer device (which may be a personal computer, a server, a network device, etc.) to perform all or part of the steps of the method according to the embodiments of the present invention. And the aforementioned storage medium includes: a usb disk, a removable hard disk, a ROM, a RAM, a magnetic disk, or an optical disk, etc.
Furthermore, it should be noted that in the system and method of the present invention, it is apparent that the components or steps may be disassembled and/or assembled. Such decomposition and/or recombination should be considered as equivalent aspects of the present invention. Also, the steps of performing the series of processes described above may naturally be performed in chronological order in the order of description, but are not necessarily performed in chronological order, and some steps may be performed in parallel or independently of each other. It will be appreciated by those of ordinary skill in the art that all or any of the steps or components of the methods and apparatus of the present invention may be implemented in hardware, firmware, software, or a combination thereof in any computing device (including processors, storage media, etc.) or network of computing devices, as would be apparent to one of ordinary skill in the art after reading this description of the invention.
The object of the invention can thus also be achieved by running a program or a set of programs on any computing device. The computing device may be a well-known general purpose device. The object of the invention can thus also be achieved by merely providing a program product containing program code for implementing said method or apparatus. That is, such a program product also constitutes the present invention, and a storage medium storing such a program product also constitutes the present invention. It is apparent that the storage medium may be any known storage medium or any storage medium developed in the future. It should also be noted that in the system and method of the present invention, it is apparent that the components or steps may be disassembled and/or assembled. Such decomposition and/or recombination should be considered as equivalent aspects of the present invention. The steps of executing the series of processes may naturally be executed in chronological order in the order described, but are not necessarily executed in chronological order. Some steps may be performed in parallel or independently of each other.
While the foregoing is directed to the preferred embodiments of the present invention, it will be appreciated by those skilled in the art that various modifications and adaptations can be made without departing from the principles of the present invention, and such modifications and adaptations are intended to be comprehended within the scope of the present invention.
Claims (10)
1. A water quality information processing method, comprising:
acquiring first water quality data of sewage to be treated;
determining the input amount of the nano material into the sewage to be treated according to the first water quality data;
acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount;
and according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold.
2. The water quality information processing method according to claim 1, wherein acquiring first water quality data of the sewage to be treated comprises:
and acquiring at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated through water quality monitoring equipment, and taking the at least one of physical parameters, chemical parameters and biological parameters of the sewage to be treated as first water quality data of the sewage to be treated.
3. The water quality information processing method according to claim 1, wherein determining an input amount of the nanomaterial to be input into the sewage to be treated based on the first water quality data comprises:
and when the first water quality data is larger than a preset water quality standard threshold value, determining the input amount of the nano material input into the sewage to be treated according to the preset water quality standard threshold value.
4. The water quality information processing method according to claim 1, wherein the preparation process of the nanomaterial comprises:
obtaining a gaseous reactant;
reacting and precipitating the gaseous reactant to obtain an intermediate solid material;
and carrying out post-treatment on the intermediate solid material to obtain the nano material.
5. The method for processing water quality information according to claim 1, wherein acquiring real-time water quality data of the sewage to which the nanomaterial is added according to the addition amount comprises:
and acquiring at least one of physical parameters, chemical parameters and biological parameters of the sewage after the nano materials are added according to the input amount by water quality monitoring equipment, and taking the at least one of the physical parameters, the chemical parameters and the biological parameters as real-time water quality data.
6. The water quality information processing method according to claim 1, wherein adjusting the input amount of the nanomaterial and the sewage treatment time according to the real-time water quality data until the real-time water quality data reaches a preset target water quality threshold value comprises:
comparing the real-time water quality data with a preset target water quality threshold value to obtain a difference;
and adjusting the input amount of the nano material and the sewage treatment time according to the difference amount.
7. The water quality information processing method according to claim 1, further comprising:
and recovering the nano material in the water when the real-time water quality data is smaller than or equal to a preset target water quality threshold value.
8. A water quality information processing system, comprising:
the acquisition module is used for acquiring first water quality data of the sewage to be treated; acquiring real-time water quality data of the sewage after the nano material is added according to the adding amount;
the treatment module is used for determining the input amount of the nano material into the sewage to be treated according to the first water quality data; and according to the real-time water quality data, adjusting the input amount of the nano material and the sewage treatment time until the real-time water quality data reaches a preset target water quality threshold.
9. A computing device, comprising: a processor, a memory storing a computer program which, when executed by the processor, performs the method of any one of claims 1 to 7.
10. A computer readable storage medium, characterized in that instructions are stored which, when run on a computer, cause the computer to perform the method of any of claims 1 to 7.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202410200850.XA CN117819637A (en) | 2024-02-23 | 2024-02-23 | Water quality information processing method and system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202410200850.XA CN117819637A (en) | 2024-02-23 | 2024-02-23 | Water quality information processing method and system |
Publications (1)
Publication Number | Publication Date |
---|---|
CN117819637A true CN117819637A (en) | 2024-04-05 |
Family
ID=90523040
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202410200850.XA Pending CN117819637A (en) | 2024-02-23 | 2024-02-23 | Water quality information processing method and system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN117819637A (en) |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107540136A (en) * | 2017-09-20 | 2018-01-05 | 深圳市尤佳环境科技有限公司 | A kind of sewage treatment process and its system |
CN112573641A (en) * | 2020-11-20 | 2021-03-30 | 中国环境科学研究院 | Sewage treatment capacity determining method and device |
CN114425187A (en) * | 2022-02-16 | 2022-05-03 | 北京航天神禾防务技术有限公司 | Multistage nanometer filter tower regulation and control system based on water quality testing |
WO2023010804A1 (en) * | 2021-08-03 | 2023-02-09 | 佛山市云米电器科技有限公司 | Water sample characteristic detection method and apparatus |
CN115893533A (en) * | 2021-08-23 | 2023-04-04 | 中国石油天然气集团有限公司 | Control system, method and treatment system for refinery sewage treatment |
CN116947180A (en) * | 2023-06-26 | 2023-10-27 | 上海矾花科技有限公司 | Chemical precipitation water treatment system and control method of chemical precipitant addition amount |
-
2024
- 2024-02-23 CN CN202410200850.XA patent/CN117819637A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107540136A (en) * | 2017-09-20 | 2018-01-05 | 深圳市尤佳环境科技有限公司 | A kind of sewage treatment process and its system |
CN112573641A (en) * | 2020-11-20 | 2021-03-30 | 中国环境科学研究院 | Sewage treatment capacity determining method and device |
WO2023010804A1 (en) * | 2021-08-03 | 2023-02-09 | 佛山市云米电器科技有限公司 | Water sample characteristic detection method and apparatus |
CN115893533A (en) * | 2021-08-23 | 2023-04-04 | 中国石油天然气集团有限公司 | Control system, method and treatment system for refinery sewage treatment |
CN114425187A (en) * | 2022-02-16 | 2022-05-03 | 北京航天神禾防务技术有限公司 | Multistage nanometer filter tower regulation and control system based on water quality testing |
CN116947180A (en) * | 2023-06-26 | 2023-10-27 | 上海矾花科技有限公司 | Chemical precipitation water treatment system and control method of chemical precipitant addition amount |
Non-Patent Citations (1)
Title |
---|
张松柏等著: "《核酸生物传感器原理及应用》", 31 December 2022, 上海科学技术出版社 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Guibal et al. | Chitosan sorbents for platinum sorption from dilute solutions | |
CN109295713B (en) | Preparation method and application of magnetic composite hydrogel based on cellulose nanofibers | |
Lagoa et al. | Evaluation of dry protonated calcium alginate beads for biosorption applications and studies of lead uptake | |
CN112552512B (en) | Polybenzimidazole derivative, preparation method thereof and application of polybenzimidazole derivative in cyclic adsorption of metal ions | |
Wang et al. | Sequential recycle of valuable phosphorus compounds of glyphosine, glyphosate, and phosphorous acid from glyphosate mother liquor by D301 resin through sorbent dosage control | |
CN105771912B (en) | A kind of multifunctional bio adsorbent material and preparation method thereof | |
CA2845239A1 (en) | Process for treating thiocyanate containing aqueous solutions | |
Massoud et al. | Preparation and characterization of poly (acrylic acid-dimethylaminoethylmethacrylate) as amphoteric exchange resin and its adsorption properties | |
CN117819637A (en) | Water quality information processing method and system | |
CN111450809A (en) | Bentonite modification method for treating industrial wastewater containing perchlorate | |
Guo et al. | Adsorption of copper ions from solution using xanthate wheat straw | |
Wong et al. | Removal and recovery of copper (II) ions by bacterial biosorption | |
Luo et al. | Adsorption of Th (IV) on glutaraldehyde cross-linked N-(4-Aminobenzoyl)-ʟ-glutamic acid modified chitosan | |
Li et al. | Novel Cr (III) surface magnetic ion-imprinted materials based on graphene oxide for selective removal of Cr (III) in aqueous solution | |
Zhou et al. | Ni (II) removal from aqueous solution by biosorption and flocculation using microbial flocculant GA1 | |
CN117550675A (en) | Preparation method of modified activated carbon capable of effectively removing phosphorus in glyphosate waste salt | |
CN114797795A (en) | By using GMA/H 3 PO 4 Method for treating uranium-containing wastewater by using modified natural fibers | |
Nagai et al. | High-recovery material for mercury ions based on a polyallylamine hydrogel with thiourea groups at cross-linking points | |
CN113070046B (en) | Preparation method of defluorination adsorbent modified by biopolymer composite material | |
Pagnanelli et al. | Mechanistic modeling of heavy metal biosorption in batch and membrane reactor systems | |
CN109499551B (en) | Phosphate-based chelate resin and preparation and uranium-containing wastewater treatment methods thereof | |
CN105000642B (en) | Treatment method of silicon-containing wastewater generated in molecular sieve preparation processes | |
Pagnanelli et al. | Effect of equilibrium models in the simulation of heavy metal biosorption in single and two-stage UF/MF membrane reactor systems | |
Ishida et al. | A new sampling method with zirconium‐loaded resin for phosphate oxygen isotope analysis in oligotrophic freshwater systems | |
CN112225415A (en) | Method for removing heavy metals by modified activated carbon mediated sludge bioleaching |
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 |