CN110434154A - Aerobic aeration type refuse landfill temperature predicting method - Google Patents

Aerobic aeration type refuse landfill temperature predicting method Download PDF

Info

Publication number
CN110434154A
CN110434154A CN201910753326.4A CN201910753326A CN110434154A CN 110434154 A CN110434154 A CN 110434154A CN 201910753326 A CN201910753326 A CN 201910753326A CN 110434154 A CN110434154 A CN 110434154A
Authority
CN
China
Prior art keywords
temperature
formula
prediction
junk
heap body
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
CN201910753326.4A
Other languages
Chinese (zh)
Inventor
刘磊
陈亿军
田宇
张�雄
姚远
魏明俐
李源
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.)
Wuhan Environmental Investment And Development Group Co ltd
Wuhan Institute of Rock and Soil Mechanics of CAS
Original Assignee
Wuhan Environmental Investment And Development Group Co ltd
Wuhan Institute of Rock and Soil Mechanics of CAS
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 Wuhan Environmental Investment And Development Group Co ltd, Wuhan Institute of Rock and Soil Mechanics of CAS filed Critical Wuhan Environmental Investment And Development Group Co ltd
Priority to CN201910753326.4A priority Critical patent/CN110434154A/en
Publication of CN110434154A publication Critical patent/CN110434154A/en
Priority to CN202010822578.0A priority patent/CN112264423B/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01KMEASURING TEMPERATURE; MEASURING QUANTITY OF HEAT; THERMALLY-SENSITIVE ELEMENTS NOT OTHERWISE PROVIDED FOR
    • G01K13/00Thermometers specially adapted for specific purposes

Landscapes

  • Physics & Mathematics (AREA)
  • General Physics & Mathematics (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention belongs to technical field of waste treatment more particularly to a kind of aerobic aeration type refuse landfill temperature predicting methods.The essential attribute parameter of refuse landfill where the prediction technique comprises determining that;Calculate temperature prediction result of the junk-heap body under essential attribute Parameter Conditions;Measure the temperature results of junk-heap body;The temperature results obtained to prediction are modified.The present invention can provide solution for the prediction of junk-heap body temperature in aerobic ventilation process, it can avoid the generation that fire and explosion accident occur for mixed gas, the efficient operation for having ensured aerobic ventilating system to greatest extent simultaneously has preferable practicability and flexibility in aerobic ventilating engineering.

Description

Aerobic aeration type refuse landfill temperature predicting method
Technical field
The invention belongs to technical field of waste treatment more particularly to a kind of aerobic aeration type refuse landfill temperature prediction sides Method.
Background technique
Aerobic ventilation is a kind of main way of refuse landfill in-situ immobilization, and technical principle is to inject air into rubbish In heap body, make the accelerated degradation under aerobic environment of the organic matter in rubbish, so that reaching reduces methane concentration, reduces Leachate site Discharge and the purpose in situ for eliminating pollution source.
Organic matter degradation rate in aerobic ventilation process is accelerated, and the temperature of junk-heap body is caused to increase.Due to sky After gas injects junk-heap body, the intracorporal methane of oxygen and rubbish heap in air occurs chemical reaction and generates carbon dioxide and water, The two synchronous consumption.But junk-heap body has strong heterogeneity, and there are left portion in some regions in whole landfill yard Methane is divided not to be consumed completely.Methane without being consumed is collected together with the oxygen constantly injected by extraction well.Work as rubbish Rubbish heap is intracorporal when the temperature is excessively high (generally more than 60 DEG C), and the mixed gas being collected into easily causes fire or explosion accident, gives The efficient and safe operation of aerobic ventilating system brings huge hidden danger.For this purpose, aerobic landfill yard is both needed to junk-heap body Temperature is monitored.When heap temperature rises to 55 DEG C or more, monitoring system is alarmed, and takes control measure to reduce Heap temperature.
Since refuse landfill takes up a large area, temperature sensor is and long-range in the intracorporal embedded limited amount of rubbish heap Control system can only alarm according to the temperature results that monitoring obtains, and existing monitoring and warning technology cannot achieve warm in heap body The prediction of degree.In addition China region is wide, the rubbish such as moisture content, organic matter in different zones garbage loading embeading attribute difference compared with Greatly, the gas injection Intensity Design of aerobic ventilation also has difference.It would therefore be highly desirable to propose that one kind can be according to live actual condition to aerobic logical The method that junk-heap body temperature is predicted during wind, the safe operation for aerobic ventilating system provide decision-making foundation.
Summary of the invention
In view of the above existing problems in the prior art, the present invention provides a kind of aerobic aeration type refuse landfill temperature predictions Method provides decision-making foundation with the safe operation for aerobic ventilating system.
The present invention through the following technical solutions to achieve the above objectives:
A kind of aerobic aeration type refuse landfill temperature predicting method, the prediction technique include:
The essential attribute parameter of refuse landfill where determining;
Calculate temperature prediction result of the junk-heap body under essential attribute Parameter Conditions;
Measure the temperature results of junk-heap body;
The temperature results obtained to prediction are modified.
Further, the essential attribute parameter of the refuse landfill includes: garbage loading embeading age, the content of organic matter, heap body Initial temperature, moisture content, gas injection intensity and injection gas temperature.
Further, the temperature prediction for calculating junk-heap body under essential attribute Parameter Conditions is as a result, specifically include:
According to formula 1) obtain rate of heat release R, the formula 1) are as follows:
R=R ' (T) * f (t ', os, QI,θ,T0,TI), formula 1);
The formula 1) in, t ' is garbage loading embeading age (yr);Os is the content of organic matter (%);QIFor gas injection intensity (m3/h); θ is moisture content (%);T0For initial temperature;TIFor the temperature for injecting gas;R ' (T) is potential rate of heat release (J m-3s-1);
Utilize formula 2) temperature prediction of the junk-heap body under essential attribute Parameter Conditions is calculated as a result, the formula 2) Are as follows:
The formula 2) in, αsFor thermal capacitance (the J m of junk-heap body-3K-1);τ is the coefficient of heat conduction (W m-1K-1);αgFor gas Thermal capacitance (the J m of body-3K-1);VgFor gas flow rate (m s-1);R is rate of heat release (J m-3s-1);T is the rubbish heap that prediction obtains Temperature;For the differential operator of temperature.
Further, the temperature results of the measurement junk-heap body, specifically include:
By the temperature sensor of junk-heap body site layout project, monitors and be averaged to obtain the temperature knot for determining junk-heap body Fruit.
Further, it predicts that obtained temperature results are modified for described pair, specifically includes:
The difference of the temperature results of the temperature results and prediction that are monitored by comparative analysis carries out the temperature configuration of prediction Compensating approach.
Further, the difference of the temperature results of the temperature results and prediction that are monitored by comparative analysis, to prediction Temperature configuration compensates and corrects, and specifically includes:
During the temperature results of contrastive detection and the temperature results of prediction, the target for optimizing calculating is that error amount is minimum Change, pass through formula 3) complete, the formula 3) are as follows:
The formula 3) in,For approximate function;F(Ti) it is the function that the temperature results data of monitoring form, n is Data bulk summation;
Based on formula 3) to the correction result of temperature, pass through formula 4) rate of heat release is modified again, the formula 4) are as follows:
R '=R*w, formula 4);
The formula 4) in, R ' is revised rate of heat release;W is modifying factor;
Obtained revised rate of heat release is introduced into formula 2) in, with the temperature prediction result after being optimized.
Further, the modifying factor passes through formula 5) obtain, the formula 5) are as follows:
W=f (Ta, T ') and formula 5);
The formula 5) in, T ' is the mean temperature result (K) that monitoring obtains;TaTo predict obtained mean temperature result (K)。
The beneficial effects of the present invention are:
A kind of aerobic aeration type refuse landfill temperature predicting method provided by the present invention, due to the prediction result of temperature It is to be calculated under conditions of the essential attribute parameter based on refuse landfill, so as to be obtained according to live actual condition The variation tendency of temperature, and can realize in advance according to field monitoring as a result, the trend to temperature change is modified to temperature The prediction and anticipation of elevation process are spent, and has ensured the reliability of prediction result, can be junk-heap body in aerobic ventilation process The prediction of temperature provides solution, can avoid the generation that fire and explosion accident occur for mixed gas, while to greatest extent The efficient operation for having ensured aerobic ventilating system has preferable practicability and flexibility in aerobic ventilating engineering.
Detailed description of the invention
To describe the technical solutions in the embodiments of the present invention more clearly, make required in being described below to embodiment Attached drawing is briefly described, it should be apparent that, drawings in the following description are only some embodiments of the invention, for For those of ordinary skill in the art, without creative efforts, it can also be obtained according to these attached drawings other Attached drawing.
Fig. 1 is a kind of flow diagram of aerobic aeration type refuse landfill temperature predicting method of the embodiment of the present invention;
Fig. 2 is revised temperature prediction result and the temperature without obtaining by modified temperature prediction result and monitoring The comparison schematic diagram of value.
Specific embodiment
Following will be combined with the drawings in the embodiments of the present invention, and technical solution in the embodiment of the present invention carries out clear, complete Site preparation description, it is clear that described embodiments are only a part of the embodiments of the present invention, instead of all the embodiments.It is based on Embodiment in the present invention, it is obtained by those of ordinary skill in the art without making creative efforts every other Embodiment shall fall within the protection scope of the present invention.
Fig. 1 is a kind of flow diagram of aerobic aeration type refuse landfill temperature predicting method of the embodiment of the present invention, In conjunction with Fig. 1, which includes:
S1: the essential attribute parameter of refuse landfill where determining;
S2: temperature prediction result of the junk-heap body under essential attribute Parameter Conditions is calculated;
S3: the temperature results of junk-heap body are measured;
S4: the temperature results obtained to prediction are modified.
A kind of aerobic aeration type refuse landfill temperature predicting method provided by the embodiment of the present invention, it is pre- due to temperature It surveys the result is that being calculated under conditions of the essential attribute parameter based on refuse landfill, so as to according to the practical work in scene Condition obtains the variation tendency of temperature, and can realize and mention according to field monitoring as a result, the trend to temperature change is modified Preceding prediction and anticipation to temperature elevation process, and ensured the reliability of prediction result, it can be rubbish in aerobic ventilation process The prediction of rubbish heap temperature provides solution, can avoid the generation that fire and explosion accident occur for mixed gas, while maximum The efficient operation for having ensured aerobic ventilating system of limit has preferable practicability and flexibility in aerobic ventilating engineering.
Specifically, in the S1 of the embodiment of the present invention, the essential attribute parameter of refuse landfill includes: garbage loading embeading age, has Machine matter content, heap body initial temperature, moisture content, gas injection intensity and injection gas temperature.
The S2 of the embodiment of the present invention is specifically included:
According to formula 1) obtain rate of heat release R, the formula 1) are as follows:
R=R ' (T) * f (t ', os, QI,θ,T0,TI), formula 1);
The formula 1) in, t ' is garbage loading embeading age (yr);Os is the content of organic matter (%);QIFor gas injection intensity (m3/h); θ is moisture content (%);T0For initial temperature;TIFor the temperature for injecting gas;R ' (T) is potential rate of heat release (J m-3s-1);
Utilize formula 2) temperature prediction of the junk-heap body under essential attribute Parameter Conditions is calculated as a result, the formula 2) it is temperature Equation of transfer is spent, the formula 2 is passed through) temperature can be calculated with the changing rule of gas injection runing time, the formula 2) Are as follows::
The formula 2) in, αsFor thermal capacitance (the J m of junk-heap body-3K-1);τ is the coefficient of heat conduction (W m-1K-1);αgFor gas Thermal capacitance (the J m of body-3K-1);VgFor gas flow rate (m s-1);R is rate of heat release (J m-3s-1);T is the rubbish heap that prediction obtains Temperature;For the differential operator of temperature.
In aerobic ventilating system operational process, when related operating parameter changes, the prediction result of temperature also can be with Change.
The S3 of the embodiment of the present invention, specifically includes:
By the temperature sensor of junk-heap body site layout project, monitors and be averaged to obtain the temperature knot for determining junk-heap body Fruit.
The S4 of the embodiment of the present invention, specifically includes:
The difference of the temperature results of the temperature results and prediction that are monitored by comparative analysis carries out the temperature configuration of prediction Compensating approach, to ensure the reliability of prediction result.
Specifically, during the temperature results of contrastive detection and the temperature results of prediction, optimize the target of calculating to miss Difference minimizes, and passes through formula 3) complete, the formula 3) are as follows:
The formula 3) in,For approximate function;F(Ti) it is the function that the temperature results data of monitoring form, n is Data bulk summation;
Based on formula 3) to the correction result of temperature, pass through formula 4) rate of heat release is modified again, the formula 4) are as follows:
R '=R*w, formula 4);
The formula 4) in, R ' is revised rate of heat release;W is modifying factor;
Obtained revised rate of heat release is introduced into formula 2) in, with the temperature prediction result after being optimized.By In by obtaining revised rate of heat release, bringing formula 2 into this way) in temperature is predicted again, the temperature predicted in this way It is worth closer to actual conditions.
The modifying factor of the embodiment of the present invention passes through formula 5) obtain, the formula 5) are as follows:
W=f (Ta, T ') and formula 5);
The formula 5) in, T ' is the mean temperature result (K) that monitoring obtains;TaTo predict obtained mean temperature result (K)。
It is specific to use:
Live aerobic ventilation experiment is carried out to certain refuse landfill demonstration place in Hubei Province, to rubbish during test The temperature value of heap body is monitored, and is corrected by monitoring obtained temperature value to prediction result, revised temperature Prediction result is closer to actual monitoring result.
The house refuse heap body landfill age at scene is 9 years, preceding 20 days rate of venting about 210m3/ h, the ventilation after 20 days Rate about 320m3/h.Ventilation monitors the intracorporal temperature of rubbish heap after starting.Prediction junk-heap body is obtained by sampling Property parameters needed for temperature are as follows: the content of organic matter 10.2%, initial aqueous rate 41.3%, and initial temperature is 31.1 DEG C, The thermal capacitance 3.4*10 of junk-heap body6(J m-3K-1), the coefficient of heat conduction is 0.23W m-1K-1, the thermal capacitance of gas is 1140J m-3K-1
Ventilation process continues 220 days, is monitored daily to rubbish temperature.It is right according to the average temperature value that monitoring obtains Heat release rate is modified, and revised temperature prediction result and the modified temperature prediction result of no process are obtained with monitoring Temperature value compare (see Fig. 2).As figure shows, it 20 days before ventilation, corrects and is more connect without modified prediction result Closely.After ventilation is lasting to be carried out, the error between temperature prediction result and monitoring result under no correction conditions obviously gradually increases Greatly.After ventilation carries out leading 60 days, the error under no correction conditions reaches 4-8 DEG C, and revised error is only 2 DEG C.By This case it is found that with ventilation progress, predict aerobic reaction caused by temperature change need to be modified parameter, after amendment Prediction result can significantly reduce prediction error.
Following illustrated embodiment is better embodiment of the invention, only is used to facilitate to illustrate the present invention, not to this hair The bright limitation made under any form has usually intellectual in any technical field, if not departing from the proposed skill of the present invention In the range of art feature, using the equivalent embodiment for locally changing or modifying made by disclosed technology contents, and Without departing from technical feature content of the invention, in the range of still falling within the technology of the present invention feature.

Claims (7)

1. a kind of aerobic aeration type refuse landfill temperature predicting method, which is characterized in that the prediction technique includes:
The essential attribute parameter of refuse landfill where determining;
Calculate temperature prediction result of the junk-heap body under essential attribute Parameter Conditions;
Measure the temperature results of junk-heap body;
The temperature results obtained to prediction are modified.
2. a kind of aerobic aeration type refuse landfill temperature predicting method according to claim 1, which is characterized in that described The essential attribute parameter of refuse landfill includes: that garbage loading embeading age, the content of organic matter, heap body initial temperature, moisture content, gas injection are strong Degree and injection gas temperature.
3. a kind of aerobic aeration type refuse landfill temperature predicting method according to claim 2, which is characterized in that described Temperature prediction of the junk-heap body under essential attribute Parameter Conditions is calculated as a result, specifically including:
According to formula 1) obtain rate of heat release R, the formula 1) are as follows:
R=R ' (T) * f (t ', os, QI,θ,T0,TI), formula 1);
The formula 1) in, t ' is garbage loading embeading age (yr);Os is the content of organic matter (%);QIFor gas injection intensity (m3/h);θ is Moisture content (%);T0For initial temperature;TIFor the temperature for injecting gas;R ' (T) is potential rate of heat release (J m-3s-1);
Utilize formula 2) temperature prediction of the junk-heap body under essential attribute Parameter Conditions is calculated as a result, the formula 2) are as follows:
The formula 2) in, αsFor thermal capacitance (the J m of junk-heap body-3 K-1);τ is the coefficient of heat conduction (W m-1 K-1);αgFor gas Thermal capacitance (J m-3 K-1);VgFor gas flow rate (m s-1);R is rate of heat release (J m-3s-1);T is the junk-heap body that prediction obtains Temperature;For the differential operator of temperature.
4. a kind of aerobic aeration type refuse landfill temperature predicting method according to claim 3, which is characterized in that described The temperature results for measuring junk-heap body, specifically include:
By the temperature sensor of junk-heap body site layout project, monitors and be averaged to obtain the temperature results for determining junk-heap body.
5. a kind of aerobic aeration type refuse landfill temperature predicting method according to claim 4, which is characterized in that described The temperature results obtained to prediction are modified, and are specifically included:
The difference of the temperature results of the temperature results and prediction that are monitored by comparative analysis, compensates the temperature configuration of prediction Amendment.
6. a kind of aerobic aeration type refuse landfill temperature predicting method according to claim 5, which is characterized in that pass through The difference of the temperature results of the temperature results and prediction of comparative analysis monitoring, compensates and corrects the temperature configuration of prediction, has Body includes:
During the temperature results of contrastive detection and the temperature results of prediction, optimizes the target of calculating and is minimized for error amount, Pass through formula 3) complete, the formula 3) are as follows:
The formula 3) in,For approximate function;F(Ti) it is the function that the temperature results data of monitoring form, n is data Quantity summation;
Based on formula 3) to the correction result of temperature, pass through formula 4) rate of heat release is modified again, the formula 4) are as follows:
R '=R*w, formula 4);
The formula 4) in, R ' is revised rate of heat release;W is modifying factor;
Obtained revised rate of heat release is introduced into formula 2) in, with the temperature prediction result after being optimized.
7. a kind of aerobic aeration type refuse landfill temperature predicting method according to claim 6, which is characterized in that described Modifying factor passes through formula 5) obtain, the formula 5) are as follows:
W=f (Ta, T ') and formula 5);
The formula 5) in, T ' is the mean temperature result (K) that monitoring obtains;TaTo predict obtained mean temperature result (K).
CN201910753326.4A 2019-08-15 2019-08-15 Aerobic aeration type refuse landfill temperature predicting method Pending CN110434154A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
CN201910753326.4A CN110434154A (en) 2019-08-15 2019-08-15 Aerobic aeration type refuse landfill temperature predicting method
CN202010822578.0A CN112264423B (en) 2019-08-15 2020-08-14 Temperature prediction method for aerobic ventilation type refuse landfill

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910753326.4A CN110434154A (en) 2019-08-15 2019-08-15 Aerobic aeration type refuse landfill temperature predicting method

Publications (1)

Publication Number Publication Date
CN110434154A true CN110434154A (en) 2019-11-12

Family

ID=68435752

Family Applications (2)

Application Number Title Priority Date Filing Date
CN201910753326.4A Pending CN110434154A (en) 2019-08-15 2019-08-15 Aerobic aeration type refuse landfill temperature predicting method
CN202010822578.0A Active CN112264423B (en) 2019-08-15 2020-08-14 Temperature prediction method for aerobic ventilation type refuse landfill

Family Applications After (1)

Application Number Title Priority Date Filing Date
CN202010822578.0A Active CN112264423B (en) 2019-08-15 2020-08-14 Temperature prediction method for aerobic ventilation type refuse landfill

Country Status (1)

Country Link
CN (2) CN110434154A (en)

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104268343B (en) * 2014-09-28 2018-01-12 北京理工大学 A kind of method of prediction of Turning Force with Artificial and temperature prediction for end mill cutting
CN105956399B (en) * 2016-04-29 2018-02-09 广州视源电子科技股份有限公司 A kind of temperature predicting method and electronic thermometer
CN206459769U (en) * 2016-11-11 2017-09-01 北京国环清华环境工程设计研究院有限公司 A kind of on-Line Monitor Device of Landfill temperature
CA3031977A1 (en) * 2018-01-31 2019-07-31 Aerobic Landfill Technologies Inc. System and methods for monitoring and controlling an aerobic landfill bioreactor

Also Published As

Publication number Publication date
CN112264423B (en) 2021-12-28
CN112264423A (en) 2021-01-26

Similar Documents

Publication Publication Date Title
Li et al. Examination of CO, CO2 and active sites formation during isothermal pyrolysis of coal at low temperatures
US11123777B2 (en) System and methods for monitoring and controlling an aerobic landfill bioreactor
Ivanova et al. The long-term settlement of landfill waste
CN110918630A (en) Remediation system and method for ectopic thermal desorption of organic contaminated soil
Zhao et al. Prediction of temperature and CO concentration fields based on BPNN in low-temperature coal oxidation
KR101246808B1 (en) Simulation system for soil characteristics change
Ko et al. Case study of controlled air addition into landfilled municipal solid waste: design, operation, and control
CN110434154A (en) Aerobic aeration type refuse landfill temperature predicting method
Castellani et al. Measuring the Biodegradability of Plastic Polymers in Olive‐Mill Waste Compost with an Experimental Apparatus
CN101993071B (en) Method and device for producing super active carbon
KR101807078B1 (en) Air circulation system for foodwaste treatment by microbial agent
CN105567362B (en) Gas hydration separation bubbling intensifying device and gas hydration separation purification intensifying device and gas purification intensifying method based on the device
CN108246791A (en) A kind of petroleum hydrocarbon contaminated soil renovation technique
Nocko et al. Heat extraction from municipal solid waste landfills
CN206413633U (en) A kind of phosphine generator
KR100702334B1 (en) Landfill stabilization system
CN209280165U (en) A kind of active coke desulphurizing elephant trunk material jam automatic detection device
Li et al. Method for Determining Spontaneous Combustion Risk in Roof Cutting Gob‐Side Entry Retaining U+ L Ventilation Goaf for Mining Safety
CN205046205U (en) Full carbon fluoride suppression device of prebake aluminium cell
West et al. Methane production of raw and composted solid waste in simulated landfill cells
Landoll et al. Kinetics study of thermal decomposition of sodium carboxylate salts
CN106434322B (en) The safe explosion-proof device and working method of continuous monitoring material fermentation
Musselman et al. Gas generation at a municipal waste combustor ash monofill-Franklin, New Hampshire
CN217846228U (en) Reaction temperature and generated gas monitoring system in reaction type material underground construction process
CN211328806U (en) Carbon product calcination tail gas treatment equipment

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
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20191112

WD01 Invention patent application deemed withdrawn after publication