CN116655214A - Sludge conditioning method, device, electronic equipment and storage medium - Google Patents

Sludge conditioning method, device, electronic equipment and storage medium Download PDF

Info

Publication number
CN116655214A
CN116655214A CN202310952829.0A CN202310952829A CN116655214A CN 116655214 A CN116655214 A CN 116655214A CN 202310952829 A CN202310952829 A CN 202310952829A CN 116655214 A CN116655214 A CN 116655214A
Authority
CN
China
Prior art keywords
sludge
conditioner
viscosity data
conditioning
viscosity
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
Application number
CN202310952829.0A
Other languages
Chinese (zh)
Inventor
李丹丹
徐绪筝
虞红波
虞天浩
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing Globegroup Zhongke Water Technology Co ltd
Original Assignee
Beijing Globegroup Zhongke Water Technology Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Beijing Globegroup Zhongke Water Technology Co ltd filed Critical Beijing Globegroup Zhongke Water Technology Co ltd
Priority to CN202310952829.0A priority Critical patent/CN116655214A/en
Publication of CN116655214A publication Critical patent/CN116655214A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • C02F11/147Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using organic substances
    • 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
    • C02F2209/09Viscosity

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The disclosure relates to the technical field of sludge conditioning, in particular to a sludge conditioning method, a device, electronic equipment and a storage medium. The sludge conditioning method comprises the following steps: acquiring first viscosity data of the sludge added with the conditioner in the stirring process; acquiring a first viscosity data fluctuation value based on the first viscosity data; and determining that the fluctuation value of the first viscosity data meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring. According to the technical scheme, the time point of complete reaction of the sludge and the conditioner can be accurately determined, the problem that the sludge dewatering effect is poor due to errors generated by judging the reaction end point of the sludge and the conditioner by means of artificial experience is solved, the problem that the end point of complete reaction of the conditioner and the sludge is inaccurate through simple sludge dewatering detection is solved, and therefore the problems that the sludge dewatering effect is poor and energy consumption is increased are solved.

Description

Sludge conditioning method, device, electronic equipment and storage medium
Technical Field
The disclosure relates to the technical field of sludge conditioning, in particular to a sludge conditioning method, a device, electronic equipment and a storage medium.
Background
Along with the continuous improvement of the urban level of China, the construction of sludge conditioning facilities is developed at a high speed, a large amount of excess sludge is generated by a sewage plant, and the water content is high, the particles are finer, so that a great deal of difficulty is brought to subsequent conditioning treatment, and the sludge conditioning is needed, so that the energy consumption and the cost of the subsequent conditioning are reduced. The traditional method for improving the sludge dewatering effect comprises physical conditioning and chemical conditioning of the sludge, and the chemical conditioning is one of the most commonly used methods due to simple operation, low price and remarkable effect.
Typical chemical conditioning agents include inorganic conditioning agents and organic conditioning agents. Inorganic or organic conditioning agent is added into the sludge, and the conditioning agent fully reacts with the sludge through stirring, so that the dewatering effect of the sludge is improved. In the sludge conditioning process, the related technical scheme relies on artificial experience to set the reaction time to determine the end point of the complete reaction of the conditioner and the sludge, or determines the end point of the complete reaction of the conditioner and the sludge through simple detection of the dehydration property of the sludge. The accuracy of determining the end point of the complete reaction of the conditioner and the sludge is low, and the condition that the conditioner and the sludge do not completely react or the reaction time is too long exists. The problem of poor sludge dewatering effect caused by incomplete reaction of the conditioner and the sludge, and the problem of energy consumption increase caused by overlong reaction time of the conditioner and the sludge.
Disclosure of Invention
In order to solve the technical problems, the disclosure provides a sludge conditioning method, a device, an electronic device and a storage medium, which can accurately determine the time point when the reaction of sludge and a conditioner is complete, avoid the problem of poor sludge dewatering effect caused by the error generated by judging the reaction end point of the sludge and the conditioner by means of artificial experience, and avoid the problem of inaccurate end point when the complete reaction of the conditioner and the sludge is determined by simple sludge dewatering detection, thereby improving the problems of poor sludge dewatering effect and increased energy consumption.
In a first aspect, the present disclosure provides a method of conditioning sludge, comprising:
acquiring first viscosity data of the sludge added with the conditioner in the stirring process;
acquiring a first viscosity data fluctuation value based on the first viscosity data;
and determining that the fluctuation value of the first viscosity data meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring.
In some embodiments, the obtaining the first viscosity data of the sludge after adding the conditioner during the stirring process includes:
and acquiring the first viscosity data of the sludge in the stirring process at preset intervals.
In some embodiments, the determining that the first viscosity data fluctuation value satisfies a condition that the sludge is fully reacted with the conditioner, stopping sludge agitation, comprises:
and determining that the fluctuation value of the first viscosity data is smaller than a first fluctuation threshold value and lasts for a first time period, and stopping sludge stirring.
In some embodiments, before obtaining the first viscosity data of the sludge after adding the conditioning agent during the stirring, the sludge conditioning method further comprises:
acquiring second viscosity data of sludge without conditioner in the stirring process;
and determining that the fluctuation value of the second viscosity data is smaller than a second fluctuation threshold value for a second duration based on the second viscosity data, and triggering to execute the acquisition of the first viscosity data of the sludge added with the conditioner in the stirring process.
In some embodiments, the sludge conditioning method further comprises:
obtaining the solid content in the sludge;
and determining the addition of the corresponding amount of the conditioner based on the corresponding relation between the solid amount in the sludge and the addition amount of the conditioner.
In some embodiments, before obtaining the first viscosity data of the sludge after adding the conditioning agent during the stirring, the sludge conditioning method further comprises:
obtaining viscosity values and capillary dehydration time of each group of sludge samples after the reaction of a plurality of groups of sludge samples and a conditioning agent is completed, wherein the volumes of the sludge samples in each group are the same, and the volumes of the conditioning agents added into the sludge samples in different groups are different;
determining a correlation coefficient between the viscosity value and the capillary dewatering time based on the viscosity value and the capillary dewatering time for each set of the sludge samples;
and determining that the correlation coefficient is greater than or equal to a correlation coefficient threshold value, and triggering and executing to acquire first viscosity data of the sludge added with the conditioner in the stirring process.
In some embodiments, the conditioning agent comprises at least one of polyacrylamide, chitosan, and starch.
In a second aspect, the present disclosure also provides a sludge conditioning apparatus comprising:
the first acquisition module is used for acquiring first viscosity data of the sludge added with the conditioner in the stirring process;
the second acquisition module is used for acquiring a first viscosity data fluctuation value based on the first viscosity data;
and the control module is used for determining that the first viscosity data fluctuation value meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring.
In a third aspect, the present disclosure also provides an electronic device, including:
a conditioner and a memory, the conditioner executing the sludge conditioning method according to the first aspect by calling a program or instructions stored in the memory.
In a fourth aspect, the present disclosure also provides a computer-readable storage medium storing a program or instructions that cause a computer to perform the sludge conditioning method of the first aspect.
Compared with the prior art, the technical scheme provided by the embodiment of the disclosure has the following advantages:
the sludge conditioning method provided by the embodiment of the disclosure comprises the steps of obtaining first viscosity data of sludge added with a conditioner in a stirring process; acquiring a first viscosity data fluctuation value based on the first viscosity data; and determining that the fluctuation value of the first viscosity data meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring. Therefore, the change of the viscosity value in the sludge conditioning process is detected on line, the fluctuation value of the first viscosity data is determined to meet the condition that the sludge and the conditioner react completely, the stirring of the sludge is stopped, the time point when the sludge and the conditioner react completely can be accurately determined, the problem that the sludge dewatering effect is poor due to errors generated by judging the reaction end point of the sludge and the conditioner by means of artificial experience is avoided, the problem that the end point of the complete reaction of the conditioner and the sludge is inaccurate due to simple sludge dewatering detection is avoided, and therefore the problems of poor sludge dewatering effect and increased energy consumption are solved, and the sludge dewatering effect is improved and the energy consumption is reduced.
Drawings
The accompanying drawings, which are incorporated in and constitute a part of this specification, illustrate embodiments consistent with the disclosure and together with the description, serve to explain the principles of the disclosure.
In order to more clearly illustrate the embodiments of the present disclosure or the solutions in the prior art, the drawings that are required for the description of the embodiments or the prior art will be briefly described below, and it will be obvious to those skilled in the art that other drawings can be obtained from these drawings without inventive effort.
Fig. 1 is a schematic flow chart of a sludge conditioning method according to an embodiment of the disclosure;
FIG. 2 is a graph of viscosity values over time during conditioning of a sludge provided in an embodiment of the present disclosure;
FIG. 3 is a graph of viscosity values and capillary dewatering time for various groups of sludge samples after completion of the reaction of the sludge samples with the conditioner in accordance with an embodiment of the present disclosure;
FIG. 4 is a graph of a fitted correlation of sludge viscosity values and capillary dewatering time provided by an embodiment of the present disclosure;
fig. 5 is a schematic structural diagram of a sludge conditioning apparatus according to an embodiment of the present disclosure;
fig. 6 is a schematic structural diagram of an electronic device according to an embodiment of the disclosure.
Detailed Description
In order that the above objects, features and advantages of the present disclosure may be more clearly understood, a further description of aspects of the present disclosure will be provided below. It should be noted that, without conflict, the embodiments of the present disclosure and features in the embodiments may be combined with each other.
In the following description, numerous specific details are set forth in order to provide a thorough understanding of the present disclosure, but the present disclosure may be practiced otherwise than as described herein; it will be apparent that the embodiments in the specification are only some, but not all, embodiments of the disclosure.
According to the sludge conditioning method provided by the embodiment of the disclosure, the change of the viscosity value in the sludge conditioning process is detected on line, the fluctuation value of the first viscosity data is determined to meet the condition that the sludge and the conditioner react completely, the sludge stirring is stopped, the time point when the sludge and the conditioner react completely can be accurately determined, the problem that the sludge dewatering effect is poor due to the fact that the error generated by judging the reaction end point of the sludge and the conditioner by means of artificial experience is avoided, and the problem that the end point when the conditioner and the sludge react completely is inaccurate due to the fact that the simple sludge dewatering detection is adopted is avoided, so that the problems of poor sludge dewatering effect and increased energy consumption are solved, and the sludge dewatering effect is improved and the energy consumption is reduced.
The sludge conditioning method, the device, the electronic equipment and the storage medium provided by the embodiment of the disclosure are exemplified below with reference to the accompanying drawings.
Fig. 1 is a schematic flow chart of a sludge conditioning method according to an embodiment of the disclosure. The method is suitable for application scenes for conditioning the sludge. The method can be performed by the sludge conditioning device provided by the embodiment of the disclosure, and the sludge conditioning device can be realized in a software and/or hardware mode. As shown in fig. 1, the sludge conditioning method comprises the following steps:
s101, acquiring first viscosity data of the sludge after the conditioner is added in the stirring process.
Specifically, a conditioning agent is added into sludge to be conditioned, for example, a sludge conditioning tank, after the conditioning agent is added, the viscosity data of the sludge is correspondingly changed along with the stirring process, and at the moment, the first viscosity data of the sludge is detected to obtain the first viscosity data of the sludge in the stirring process after the conditioning agent is added.
Illustratively, a viscosity acquisition device is installed in the sludge conditioning tank, and first viscosity data of the sludge is acquired through the viscosity acquisition device so as to acquire the first viscosity data of the sludge in the stirring process after the conditioner is added.
Wherein the conditioning agent comprises at least one of polyacrylamide, chitosan and starch. For example, when conditioning sludge, adding any one conditioner selected from polyacrylamide, chitosan and starch into a sludge conditioning tank; or adding any two conditioning agents of polyacrylamide, chitosan and starch into the sludge conditioning tank; or adding polyacrylamide, chitosan and starch into the sludge conditioning tank; the embodiments of the present disclosure are not particularly limited thereto.
In some embodiments, obtaining first viscosity data of sludge after adding a conditioning agent during agitation includes:
and acquiring first viscosity data of the sludge in the stirring process at intervals of a preset time length.
Specifically, the first viscosity data of the sludge during the stirring process is obtained by a viscosity acquisition device such as, but not limited to, a viscosity sensor provided in the sludge conditioning tank. The viscosity sensor may be configured to acquire first viscosity data of the sludge during the stirring process at a certain frequency, for example, at intervals of a preset duration, for example, every 1 second.
In some embodiments, the first viscosity data of the sludge during the stirring process may also be obtained in real time. And compared with the method for acquiring the first viscosity data of the sludge in the stirring process in real time, the method for acquiring the first viscosity data of the sludge in the stirring process by setting the interval preset time length can reduce the power consumption of the viscosity sensor.
In other embodiments, other technical means known to those skilled in the art may be used to obtain the first viscosity data of the sludge during the stirring process, which is not specifically limited herein.
S102, acquiring a first viscosity data fluctuation value based on the first viscosity data.
Specifically, in combination with the above, first viscosity data of the primary sludge in the stirring process is obtained every interval for a preset period of time, and a change value of the first viscosity data obtained in two adjacent times is used as a first viscosity data fluctuation value.
Illustratively, the first viscosity data of the sludge during agitation is set to be acquired every 1 second. For example, the first viscosity data acquired at 5 th second is N1, the first viscosity data acquired at 6 th second is N2, the first viscosity data acquired at 7 th second is N3, the change values of N2 and N1 are the first viscosity data fluctuation values, and the change values of N3 and N2 are the first viscosity data fluctuation values.
Thereby, a first viscosity data fluctuation value is obtained from the first viscosity data.
S103, determining that the fluctuation value of the first viscosity data meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring.
Specifically, whether the condition that the sludge is completely reacted with the conditioner is satisfied is judged based on the obtained first viscosity data fluctuation value. If the condition that the sludge and the conditioner react completely is judged to be met based on the fluctuation value of the first viscosity data, the sludge and the conditioner can be determined to react completely, and the stirring of the sludge is stopped so as to carry out the next treatment of the sludge. If the condition that the sludge and the conditioner react completely is judged to be not met based on the fluctuation value of the first viscosity data, the condition that the sludge and the conditioner react incompletely can be determined, and then the sludge stirring is continued.
Therefore, the method for detecting the viscosity value of the sludge is simple, the problem of poor sludge dewatering effect caused by the error generated by judging the reaction end point of the sludge and the conditioner by means of artificial experience is avoided, and the problem of inaccurate end point of the complete reaction of the conditioner and the sludge by means of simple sludge dewatering detection is avoided, so that the problems of poor sludge dewatering effect and increased energy consumption are solved.
In addition, problems in the sludge conditioning process can be found in time according to the online detection viscosity data, and responses can be made in time. For example, the stirring speed is unreasonably set, so that the fluidity of the sludge is small, the viscosity value of the sludge does not change greatly before and after the conditioner is added, and at the moment, the stirring speed is unreasonably judged, and the stirring speed is increased.
In some embodiments, determining that the first viscosity data fluctuation value satisfies a condition that the sludge is fully reacted with the conditioning agent, stopping sludge agitation comprises:
and determining that the fluctuation value of the first viscosity data is smaller than a first fluctuation threshold value and lasts for a first time period, and stopping sludge stirring.
Specifically, based on the obtained first viscosity data fluctuation value, when the first viscosity data fluctuation value is smaller than a first fluctuation threshold value and the first time is continued, the conditioner and the sludge are determined to be completely subjected to conditioning reaction, at the moment, the sludge stirring is stopped, and the sludge can be subjected to the next treatment.
For example, the fluctuation value of the first viscosity data is smaller than the first fluctuation threshold value, for example, 1, within a first time period, for example, within 30 seconds, and the viscosity data is judged to be basically unchanged or changed very weakly in the sludge reaction process, namely, the viscosity of the sludge is stabilized, and at the moment, the conditioner and the sludge are determined to be completely subjected to conditioning reaction, and the sludge stirring is stopped.
Illustratively, fig. 2 is a graph of viscosity values over time during conditioning of a sludge provided by embodiments of the present disclosure. In fig. 2, the abscissa represents the reaction time T in S, the ordinate represents the viscosity CP in mpa×s. As shown in fig. 2, conditioning agent was added at 100s as indicated by the arrow, after which first viscosity data was obtained once every second. The viscosity of the sludge continuously obtained within 570s-600s is basically stable, namely the fluctuation value of the first viscosity data is basically unchanged or is changed very weakly within 30s, at the moment, the complete conditioning reaction of the conditioner and the sludge can be determined at 600s, and the stirring of the sludge can be stopped.
In some embodiments, the sludge conditioning method further comprises:
obtaining the solid content in the sludge;
and determining the addition of the corresponding amount of the conditioner based on the corresponding relation between the solid amount in the sludge and the addition amount of the conditioner.
Specifically, the water content of the sludge is obtained before the conditioner is added, and the solid content of the sludge is determined by the water content of the sludge. After the solid content of the sludge is obtained, the corresponding relation between the solid content of the sludge and the addition amount of the conditioner can be directly inquired, and the addition of the conditioner with the corresponding amount is determined according to the corresponding relation. Therefore, the solid quantity of the sludge to be conditioned is determined, and the corresponding quantity of the conditioner is added, so that the optimal conditioning effect is ensured, and the sludge dewatering effect is improved.
The corresponding relation between the solid amount of the sludge and the addition amount of the conditioner can be calibrated in advance. The water content of the obtained sludge can be detected by means well known to those skilled in the art, and is not described in detail herein.
In some embodiments, prior to obtaining the first viscosity data of the sludge after adding the conditioning agent during the agitation, the sludge conditioning method further comprises:
acquiring second viscosity data of sludge without conditioner in the stirring process;
and determining that the fluctuation value of the second viscosity data is smaller than a second fluctuation threshold value for a second duration based on the second viscosity data, and triggering to execute the acquisition of the first viscosity data of the sludge added with the conditioner in the stirring process.
Specifically, stirring of the sludge is started at a constant rotational speed before adding the conditioner to the sludge to be conditioned, for example, in a sludge conditioning tank, and second viscosity data of the sludge to which the conditioner is not added during stirring is measured.
And determining a second viscosity data fluctuation value based on the acquired second viscosity data, and when the acquired second viscosity data fluctuation value is smaller than a second fluctuation threshold value, continuing for a second duration. For example, the first viscosity data fluctuation values are smaller than the second fluctuation threshold value, for example, 0.4, within the second time period, for example, within 20 seconds, so that the viscosity of the sludge can be judged to be stable, the sludge can be determined to be uniformly mixed, and then the conditioner is added into the sludge, so that the conditioner is favorably contacted with the sludge sufficiently, the reaction rate is favorably improved, and the sludge conditioning efficiency is improved.
In some embodiments, prior to obtaining the first viscosity data of the sludge after adding the conditioning agent during the agitation, the sludge conditioning method further comprises:
obtaining the viscosity value and capillary dehydration time of each group of sludge samples after the reaction of a plurality of groups of sludge samples and the conditioner is completed, wherein the volumes of the sludge samples are the same, and the volumes of the conditioners added by the sludge samples in different groups are different;
determining a correlation coefficient between the viscosity value and the capillary dewatering time based on the viscosity value and the capillary dewatering time of each set of sludge samples;
and determining that the correlation coefficient is greater than or equal to a correlation coefficient threshold value, and triggering and executing to acquire first viscosity data of the sludge added with the conditioner in the stirring process.
Specifically, the same sludge sample is taken and divided into multiple groups, such as, but not limited to, five groups of sludge samples. And after the sludge samples of each group are reacted with the conditioner completely, obtaining the viscosity value and capillary dehydration time of the sludge samples of each group after the sludge samples of each group are reacted with the conditioner completely.
Illustratively, the five sets of sludge samples include set a, set B, set C, set D, and set E. Adding a first volume of conditioner to the group A sludge samples, adding a second volume of conditioner to the group B sludge samples, adding a third volume of conditioner to the group C sludge samples, adding a fourth volume of conditioner to the group D sludge samples, and adding a fifth volume of conditioner to the group E sludge samples. After the complete reaction of each group of sludge samples with the conditioner is determined, the viscosity value and capillary dewatering time of each group of sludge samples are measured to obtain the viscosity value and capillary dewatering time of each group of sludge samples after the completion of the reaction of the plurality of groups of sludge samples with the conditioner.
After the viscosity value and the capillary dewatering time of each group of sludge samples are obtained, the viscosity value and the capillary dewatering time of each group of sludge samples are input into Excel JMP data processing software for data correlation analysis, so that the corresponding correlation coefficient R is obtained 2 . When the correlation coefficient R 2 When the viscosity value is larger than or equal to a correlation coefficient threshold value, for example, 0.9, the viscosity value and the capillary dewatering time can be judged to have stronger correlation, namely, the acquired data are effective, and the sludge can be conditioned by adopting the sludge online conditioning method provided by the embodiment of the disclosureCan realize better sludge conditioning effect. When the correlation coefficient R 2 The viscosity value and the capillary dewatering time are considered to have weak correlation or no correlation when the viscosity value is smaller than the correlation coefficient threshold value, for example, 0.9, the effectiveness of the viscosity value in the sludge conditioning process is low or invalid in the online detection, and the sludge is conditioned by adopting the sludge online conditioning method provided by the embodiment of the disclosure, so that the dewatering effect of the sludge is poor.
Illustratively, fig. 3 is a graph of viscosity values and capillary dewatering time for various groups of sludge samples after completion of a reaction of the sludge samples with a conditioner, as provided by embodiments of the present disclosure. Fig. 4 is a graph of a fitted correlation of sludge viscosity values and capillary dewatering time provided in an embodiment of the present disclosure. In fig. 3, the abscissa represents the volume V of the conditioning agent in ml, the left side of the ordinate represents the capillary dewatering time CTS in S, and the right side viscosity CP in mPa x S; in fig. 4, the abscissa represents the fine dewatering time CTS in S, and the ordinate represents the viscosity CP in mpa×s. The curve obtained in fig. 4 is obtained by performing correlation fitting on the viscosity values and capillary dewatering time data obtained from the multiple sets of sludge samples in fig. 3. As shown in FIG. 4, the capillary dewatering time CST of sludge is positively correlated with the viscosity of sludge, and the correlation coefficient R 2 And 0.902, which shows that the capillary dehydration time of the sludge has a strong correlation with the viscosity of the sludge.
The sludge conditioning method provided by the embodiment of the disclosure comprises the steps of obtaining first viscosity data of sludge added with a conditioner in a stirring process; acquiring a first viscosity data fluctuation value based on the first viscosity data; and determining that the fluctuation value of the first viscosity data meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring. Therefore, the change of the viscosity value in the sludge conditioning process is detected on line, the fluctuation value of the first viscosity data is determined to meet the condition that the sludge and the conditioner react completely, the stirring of the sludge is stopped, the time point when the sludge and the conditioner react completely can be accurately determined, the problem that the sludge dewatering effect is poor due to errors generated by judging the reaction end point of the sludge and the conditioner by means of artificial experience is avoided, the problem that the end point of the complete reaction of the conditioner and the sludge is inaccurate due to simple sludge dewatering detection is avoided, and the problems that the sludge dewatering effect is poor and the energy consumption is increased are solved.
Based on the same inventive concept, the disclosure also provides a sludge conditioning device. Fig. 5 is a schematic structural diagram of a sludge conditioning apparatus according to an embodiment of the present disclosure. As shown in fig. 5, the sludge conditioning apparatus includes: a first obtaining module 51, configured to obtain first viscosity data of the sludge after the conditioner is added during the stirring process; a second acquisition module 52 for acquiring a first viscosity data fluctuation value based on the first viscosity data; the control module 53 is configured to determine that the first viscosity data fluctuation value satisfies a condition that the sludge and the conditioner react completely, and stop sludge stirring.
The sludge conditioning device provided in the above embodiments can perform any one of the sludge conditioning methods provided in the above embodiments, and has the same or corresponding beneficial effects, and will not be described in detail herein.
The disclosed embodiments also provide a computer storage medium storing a program or instructions that cause a computer to perform the steps of any one of the sludge conditioning methods provided in the above embodiments.
Illustratively, the program or instructions cause the computer to perform a sludge conditioning method comprising:
acquiring first viscosity data of the sludge added with the conditioner in the stirring process;
acquiring a first viscosity data fluctuation value based on the first viscosity data;
and determining that the fluctuation value of the first viscosity data meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring.
In some embodiments, the computer executable instructions, when executed by the computer conditioner, may also be used to implement the technical solutions of any of the sludge conditioning methods provided by the embodiments of the present disclosure, achieving corresponding beneficial effects.
From the above description of embodiments, it will be apparent to those skilled in the art that the present disclosure may be implemented by means of software and necessary general purpose hardware, but may of course also be implemented by means of hardware, although in many cases the former is a preferred embodiment. Based on such understanding, the technical solution of the present disclosure may be embodied essentially or in a part contributing to the prior art in the form of a software product, which may be stored in a computer readable storage medium, such as a floppy disk, a Read-Only Memory (ROM), a random access Memory (Random Access Memory, RAM), a FLASH Memory (FLASH), a hard disk or an optical disk of a computer, etc., including several instructions for causing a computer device (which may be a personal computer, a server, or a network device, etc.) to perform the sludge conditioning method in the various embodiments of the present invention.
On the basis of the implementation manner, the embodiment of the disclosure also provides electronic equipment. The electronic device includes: a conditioner and a memory; the conditioner is used for executing the steps of any sludge conditioning method provided by the embodiment by calling the program or the instruction stored in the memory, so that the corresponding beneficial effects are realized.
Fig. 6 is a schematic hardware structure of an electronic device according to an embodiment of the disclosure. As shown in fig. 6, the electronic device includes one or more conditioners 501 and a memory 502. The conditioner 501 may be a central conditioning unit (CPU) or other form of conditioning unit having data conditioning capabilities and/or instruction execution capabilities, and may control other components in the electronic device to perform desired functions.
Memory 502 may include one or more computer program products that may include various forms of computer-readable storage media, such as volatile memory and/or non-volatile memory. The volatile memory may include, for example, random Access Memory (RAM) and/or cache memory (cache), and the like. The non-volatile memory may include, for example, read Only Memory (ROM), hard disk, flash memory, and the like. One or more computer program instructions may be stored on the computer readable storage medium, which the conditioner 501 may execute to implement the methods of embodiments of the present disclosure described above, and/or other desired functions. Various contents such as an input signal, a signal component, a noise component, and the like may also be stored in the computer-readable storage medium.
In one example, the electronic device may further include: an input device 503 and an output device 504, which are interconnected by a bus system and/or other form of connection mechanism (not shown).
In addition, the input device 503 may also include, for example, a keyboard, a mouse, and the like.
The output device 504 may output various information to the outside, including the determined distance information, direction information, and the like. The output device 504 may include, for example, a display, speakers, a printer, and a communication network and remote output apparatus connected thereto, etc.
Of course, only some of the components of the electronic device relevant to the present disclosure are shown in fig. 6, with components such as buses, input/output interfaces, etc. omitted for simplicity. In addition, the electronic device may include any other suitable components depending on the particular application.
It should be noted that in this document, relational terms such as "first" and "second" and the like are used solely to distinguish one entity or action from another entity or action without necessarily requiring or implying any actual such relationship or order between such entities or actions. Moreover, the terms "comprises," "comprising," or any other variation thereof, are intended to cover a non-exclusive inclusion, such that a process, method, article, or apparatus that comprises a list of elements does not include only those elements but may include other elements not expressly listed or inherent to such process, method, article, or apparatus. Without further limitation, an element defined by the phrase "comprising one … …" does not exclude the presence of other like elements in a process, method, article, or apparatus that comprises the element.
The foregoing is merely a specific embodiment of the disclosure to enable one skilled in the art to understand or practice the disclosure. Various modifications to these embodiments will be readily apparent to those skilled in the art, and the generic principles defined herein may be applied to other embodiments without departing from the spirit or scope of the disclosure. Thus, the present disclosure is not intended to be limited to the embodiments shown and described herein but is to be accorded the widest scope consistent with the principles and novel features disclosed herein.

Claims (10)

1. A method of conditioning sludge, comprising:
acquiring first viscosity data of the sludge added with the conditioner in the stirring process;
acquiring a first viscosity data fluctuation value based on the first viscosity data;
and determining that the fluctuation value of the first viscosity data meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring.
2. The method for conditioning sludge according to claim 1, wherein the obtaining of the first viscosity data of the sludge after adding the conditioning agent during the stirring process comprises:
and acquiring the first viscosity data of the sludge in the stirring process at preset intervals.
3. The method of conditioning sludge according to claim 1, wherein said determining that the first viscosity data fluctuation value satisfies a condition that the sludge is completely reacted with the conditioner, stopping sludge agitation, comprises:
and determining that the fluctuation value of the first viscosity data is smaller than a first fluctuation threshold value and lasts for a first time period, and stopping sludge stirring.
4. The sludge conditioning method of claim 1 further comprising:
obtaining the solid content in the sludge;
and determining the addition of the corresponding amount of the conditioner based on the corresponding relation between the solid amount in the sludge and the addition amount of the conditioner.
5. The method of claim 1, further comprising, prior to obtaining the first viscosity data of the sludge after adding the conditioning agent during the agitating step:
acquiring second viscosity data of sludge without conditioner in the stirring process;
and based on the second viscosity data, determining that the fluctuation value of the second viscosity data is smaller than a second fluctuation threshold value for a second duration, and triggering to execute the acquisition of the first viscosity data of the sludge added with the conditioner in the stirring process.
6. The method for conditioning sludge according to claim 1, further comprising, before obtaining the first viscosity data of the sludge after adding the conditioning agent during the stirring process:
obtaining viscosity values and capillary dehydration time of each group of sludge samples after the reaction of a plurality of groups of sludge samples and a conditioning agent is completed, wherein the volumes of the sludge samples in each group are the same, and the volumes of the conditioning agents added into the sludge samples in different groups are different;
determining a correlation coefficient between the viscosity value and the capillary dewatering time based on the viscosity value and the capillary dewatering time for each set of the sludge samples;
and determining that the correlation coefficient is greater than or equal to a correlation coefficient threshold value, and triggering and executing to acquire first viscosity data of the sludge added with the conditioner in the stirring process.
7. The method of claim 1, wherein the conditioning agent comprises at least one of polyacrylamide, chitosan, and starch.
8. A sludge conditioning apparatus, comprising:
the first acquisition module is used for acquiring first viscosity data of the sludge added with the conditioner in the stirring process;
the second acquisition module is used for acquiring a first viscosity data fluctuation value based on the first viscosity data;
and the control module is used for determining that the first viscosity data fluctuation value meets the condition that the sludge and the conditioner react completely, and stopping sludge stirring.
9. An electronic device, comprising:
a conditioner and a memory, the conditioner performing the sludge conditioning method of any one of claims 1-7 by calling a program or instructions stored by the memory.
10. A computer-readable storage medium storing a program or instructions that cause a computer to perform the sludge conditioning method of any one of claims 1-7.
CN202310952829.0A 2023-08-01 2023-08-01 Sludge conditioning method, device, electronic equipment and storage medium Pending CN116655214A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310952829.0A CN116655214A (en) 2023-08-01 2023-08-01 Sludge conditioning method, device, electronic equipment and storage medium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310952829.0A CN116655214A (en) 2023-08-01 2023-08-01 Sludge conditioning method, device, electronic equipment and storage medium

Publications (1)

Publication Number Publication Date
CN116655214A true CN116655214A (en) 2023-08-29

Family

ID=87724641

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310952829.0A Pending CN116655214A (en) 2023-08-01 2023-08-01 Sludge conditioning method, device, electronic equipment and storage medium

Country Status (1)

Country Link
CN (1) CN116655214A (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56115695A (en) * 1980-02-20 1981-09-10 Hitachi Ltd Chemical dosage control unit in sludge treatment process
JP2005218959A (en) * 2004-02-05 2005-08-18 Kurita Water Ind Ltd High moisture content mud treatment method, high moisture content mud treating agent, and method for making granulated soil from high moisture content mud
JP2008302295A (en) * 2007-06-07 2008-12-18 Panasonic Corp Method of measuring treatment condition of sludge and sludge reduction system using it
CN110498590A (en) * 2019-08-29 2019-11-26 安徽省通源环境节能股份有限公司 A kind of sludge conditioning system and Opsonizing method
CN210656663U (en) * 2019-05-08 2020-06-02 安徽中环环保科技股份有限公司 Automatic dosing system for sludge conditioning

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56115695A (en) * 1980-02-20 1981-09-10 Hitachi Ltd Chemical dosage control unit in sludge treatment process
JP2005218959A (en) * 2004-02-05 2005-08-18 Kurita Water Ind Ltd High moisture content mud treatment method, high moisture content mud treating agent, and method for making granulated soil from high moisture content mud
JP2008302295A (en) * 2007-06-07 2008-12-18 Panasonic Corp Method of measuring treatment condition of sludge and sludge reduction system using it
CN210656663U (en) * 2019-05-08 2020-06-02 安徽中环环保科技股份有限公司 Automatic dosing system for sludge conditioning
CN110498590A (en) * 2019-08-29 2019-11-26 安徽省通源环境节能股份有限公司 A kind of sludge conditioning system and Opsonizing method

Similar Documents

Publication Publication Date Title
Sin et al. A critical comparison of systematic calibration protocols for activated sludge models: A SWOT analysis
CN105183592B (en) Method and apparatus for supporting performance evaluation
Wind et al. Environmental concentrations of boron, LAS, EDTA, NTA and Triclosan simulated with GREAT-ER in the river Itter
CN115048613B (en) Index homogenization conversion method and device, electronic equipment and storage medium
Tuerk et al. Mixture models reveal multiple positional bias types in RNA-Seq data and lead to accurate transcript concentration estimates
CN113449703B (en) Quality control method and device for environment online monitoring data, storage medium and equipment
CN116655214A (en) Sludge conditioning method, device, electronic equipment and storage medium
CN111426804A (en) Method and device for judging ozone generation sensitivity based on observation data
US20220411858A1 (en) Random emulsification digital absolute quantitative analysis method and device
Mehl et al. Calculating chemical speciation, pH, saturation index and calcium carbonate precipitation potential (CCPP) based on alkalinity and acidity using OpenModelica
US5531905A (en) System and method to control laundry waste water treatment
JP4042422B2 (en) Automatic measuring device, automatic measuring method and control method of aqueous processing agent concentration
CN113626340A (en) Test requirement identification method and device, electronic equipment and storage medium
Klein et al. Integrative Analysis of Histone ChIP‐seq and RNA‐seq Data
Catenacci et al. Early prediction of BMP tests: A step response method for estimating first-order model parameters
CN112733784A (en) Neural network training method for determining whether charging amount of desulfurized gypsum is appropriate
Sohn A non-linear temperature–time program for non-isothermal kinetic measurements
CN113156920B (en) Method, device, equipment and medium for detecting noise interference of PD controller
Constantino The effect of sewage effluent on trace metal speciation: Implications for the biotic ligand model approach
JP3120561B2 (en) How to monitor sludge digester
CN113868983B (en) Aerobic granular sludge treatment method and system based on CFD modeling simulation
Mitchell et al. Standardization of methodology for chemical functions in starch derivatives. Part 2
CN113435058B (en) Data dimension reduction method, system, terminal and medium for distribution network self-healing test model
CN112921588B (en) Washing machine control method, device, equipment and storage medium
CN111459485B (en) Evaluation method and device of transaction interface

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