CN109650517A - Utilize the control method and system of supercritical water oxidation processing organic liquid waste - Google Patents
Utilize the control method and system of supercritical water oxidation processing organic liquid waste Download PDFInfo
- Publication number
- CN109650517A CN109650517A CN201910093699.3A CN201910093699A CN109650517A CN 109650517 A CN109650517 A CN 109650517A CN 201910093699 A CN201910093699 A CN 201910093699A CN 109650517 A CN109650517 A CN 109650517A
- Authority
- CN
- China
- Prior art keywords
- organic liquid
- conversion zone
- liquid waste
- temperature
- toc
- 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
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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/06—Controlling or monitoring parameters in water treatment pH
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/08—Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
Abstract
The present invention provides a kind of control method and system using supercritical water oxidation processing organic liquid waste, this method comprises: the Current Temperatures and pressure of monitoring inside reactor conversion zone;According to the heating device and pressure-control valve of the Current Temperatures of conversion zone and pressure control reactor, the temperature and pressure of conversion zone is set to be all satisfied preset supercritical water oxidation condition, the organic liquid waste and hydrogen peroxide for being transported to inside reactor carry out supercritical water oxidation under current reaction condition;During supercritical water oxidation, control cooler carries out cooling and gas-liquid separating treatment to reactant;Monitor TOC value, COD value and pH value that gas-liquid separation processing generates liquid, and the temperature of the feed flow and/or conversion zone according to TOC value or COD value adjustment organic liquid waste.TOC in reactant or COD is carried out feedback with the feed flow of organic liquid waste and is associated with by the present invention, carries out response regulatory by feedback, so that fully reacting, secondary amount of waste are few.
Description
Technical field
The present invention relates to organic liquid waste processing technology fields more particularly to a kind of utilization supercritical water oxidation to handle organic waste
The control method and system of liquid.
Background technique
It is so-called overcritical, refer to a kind of special state of flowing material.When the fluid increasing temperature and pressure for being in vapor-liquid equilibrium
When, thermal expansion causes fluid density to reduce, and the raising of pressure makes the phase interface of vehicle repair major disappear, and becomes homogeneous system,
Here it is critical points.It is known as when the temperature of fluid, pressure are respectively higher than critical-temperature and critical pressure in supercritical state
State.Supercritical fluid has the good fluidity of similar gas, but density is much larger than gas again, therefore has many unique reasons
Change property.The critical point of water is 374.3 DEG C of temperature, pressure 22.064MPa, if by the temperature of water, pressure rise to critical point
More than, as supercritical water, the basic performances such as density, viscosity, conductivity, dielectric constant have very big difference with light water,
Show the property similar to nonpolar organic compound.Therefore, supercritical water can be with apolar substance (such as hydro carbons) and other
Organic matter dissolves each other completely, and inorganic matter especially salt, the dissociation constant and solubility in supercritical water are but very low.Meanwhile
Supercritical water can dissolve each other completely with gases such as air, oxygen, nitrogen and carbon dioxide.
Supercritical water oxidation (Supercritical Water Oxidation, abbreviation SCWO) technology is a kind of can be achieved
A variety of debirs are carried out with the technology of deep oxidation processing.The principle of supercritical Water Oxidation Technology is with supercritical water for reaction
Organic matter complete oxidation is clean H by homogeneous oxidation reaction by medium2O、CO2And N2Equal substances, S, P etc. are converted into
Highest price salt stabilizes, and heavy metal oxidation stable solid phase is present in ash content.Since supercritical water is equal to organic matter and oxygen
It is fabulous solvent, therefore the oxidation of organic matter can carry out in oxygen-enriched homogeneous phase, there is no because needing alternate turn for reaction
The limitation for moving and generating.Meanwhile 400~600 DEG C of high reaction temperature also accelerates reaction speed, it can be in reaction in several seconds
In, that is, it can reach 99% or more destructive rate.In addition, supercritical water oxidation is to a certain extent and simple burned
Journey is similar, and a large amount of heat is released in oxidation process.
SCWO technology has achieved biggish success in terms of handling various waste water and excess sludge, the disadvantage is that reaction item
Part is harsh and has very strong corrosivity to metal, and also longer to the stable compound oxidation required time of certain chemical property.
Therefore, how using SCWO progress organic liquid waste processing, to accelerate reaction speed, the reduction reaction time, add reaction more
It is of great significance entirely.
Summary of the invention
In view of the above problems, it proposes on the present invention overcomes the above problem or at least be partially solved in order to provide one kind
State the control method and system using supercritical water oxidation processing organic liquid waste of problem.
One aspect of the present invention provides a kind of control method using supercritical water oxidation processing organic liquid waste, institute
The method of stating includes:
Monitor the Current Temperatures and pressure of inside reactor conversion zone;
Control heating device and the pressure control of the reactor respectively according to the Current Temperatures of the conversion zone and pressure
Valve processed is transported to reaction so that the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition
Organic liquid waste and hydrogen peroxide inside device carry out supercritical water oxidation under current reaction condition;
During supercritical water oxidation, control cooler carries out at cooling and gas-liquid separation the reactant of generation
Reason;
TOC value, COD value and the pH value that liquid is generated after gas-liquid separation is handled are monitored, and according to the TOC value or COD value
Adjust the feed flow of the organic liquid waste and/or the temperature of the conversion zone.
Optionally, before the Current Temperatures of the monitoring inside reactor conversion zone and pressure, the method is also wrapped
It includes:
The temperature of inside reactor preheated zone is monitored, the reactor includes at least preheated zone and conversion zone;
When the temperature of the preheated zone reaches the first temperature threshold, organic liquid waste and hydrogen peroxide are controlled according to initially setting
Constant flow is transported to the conversion zone of the reactor.
Optionally, described that the feed flow of the organic liquid waste and/or described anti-is adjusted according to the TOC value or COD value
Answer the temperature in region, comprising:
When the COD value is greater than the first COD feedback threshold, the feed flow of the organic liquid waste is reduced, and open institute
The heating device of reactor is stated, so that the temperature of the conversion zone is maintained at 650 DEG C or more;
Or,
When the TOC value is greater than the first TOC feedback threshold, the feed flow of the organic liquid waste is reduced, and open institute
The heating device of reactor is stated, so that the temperature of the conversion zone is maintained at 650 DEG C or more.
Optionally, the method also includes:
When the COD value is less than the 2nd COD feedback threshold, restore the initial setting flow of the organic liquid waste, closes
The heating device of the reactor, the 2nd COD feedback threshold are less than the first COD feedback threshold;
Or,
When the TOC value is less than the 2nd TOC feedback threshold, restore the initial setting flow of the organic liquid waste, closes
The heating device of the reactor, the 2nd TOC feedback threshold are less than the first TOC feedback threshold.
Optionally, described when the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition
When, according to the conveying of initial setting flow control organic liquid waste and hydrogen peroxide, comprising:
When the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition, dioxygen is controlled
Water pump is opened, and conveys hydrogen peroxide to inside reactor according to the corresponding initial setting flow of hydrogen peroxide;
After the temperature and pressure of the conversion zone keeps stable state in predetermined time period, control material conveying
Pump is opened, and conveys organic liquid waste to inside reactor according to the corresponding initial setting flow of material.
Another aspect of the present invention provides a kind of control system using supercritical water oxidation processing organic liquid waste,
The system comprises:
First monitoring modular, for monitoring the Current Temperatures and pressure of inside reactor conversion zone;
Reaction controlling module, for controlling the reactor respectively according to the Current Temperatures and pressure of the conversion zone
Heating device and pressure-control valve, so that the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation
Condition, the organic liquid waste and hydrogen peroxide for being transported to inside reactor carry out supercritical water oxidation under current reaction condition;
Cooling control module, for during supercritical water oxidation, control cooler to the reactant of generation into
Row cooling and gas-liquid separating treatment;
Feedback control module, for monitor gas-liquid separation processing after generate liquid TOC value, COD value and pH value, and according to
The TOC value or COD value adjust the feed flow of the organic liquid waste and/or the temperature of the conversion zone.
Optionally, the system also includes:
Second monitoring modular, in the first monitoring module monitors inside reactor conversion zone Current Temperatures and
Before pressure, the temperature of inside reactor preheated zone is monitored, the reactor includes at least preheated zone and conversion zone;
Control module is fed, for controlling organic liquid waste when the temperature of the preheated zone reaches the first temperature threshold
The conversion zone of the reactor is transported to according to initial setting flow with hydrogen peroxide.
Optionally, the feedback control module is specifically used for reducing when the COD value is greater than the first COD feedback threshold
The feed flow of the organic liquid waste, and the heating device of the reactor is opened, so that the temperature of the conversion zone is kept
At 650 DEG C or more, when the COD value is less than the 2nd COD feedback threshold, restore the initial setting flow of the organic liquid waste,
The heating device of the reactor is closed, the 2nd COD feedback threshold is less than the first COD feedback threshold;
Or,
When the TOC value is greater than the first TOC feedback threshold, the feed flow of the organic liquid waste is reduced, and open institute
The heating device of reactor is stated, so that the temperature of the conversion zone is maintained at 650 DEG C or more, when the TOC value is less than second
When TOC feedback threshold, restore the initial setting flow of the organic liquid waste, closes the heating device of the reactor, described
Two TOC feedback thresholds are less than the first TOC feedback threshold.
In addition, it is stored thereon with computer program the present invention also provides a kind of computer readable storage medium, the program
The step of method as described above is realized when being executed by processor.
In addition, the present invention also provides a kind of control equipment, including memory, processor and storage are on a memory and can
The step of computer program run on a processor, the processor realizes method as described above when executing described program.
Control method and system provided in an embodiment of the present invention using supercritical water oxidation processing organic liquid waste, the present invention
TOC value in reactant or COD value are carried out feedback with the feed flow of organic liquid waste to be associated with, pass through TOC value or COD value feedback pair
Reaction is regulated and controled, and is accelerated reaction speed, is reduced the reaction time, so that fully reacting, secondary amount of waste is few, clean environment is friendly
It is good.
The above description is only an overview of the technical scheme of the present invention, in order to better understand the technical means of the present invention,
And it can be implemented in accordance with the contents of the specification, and in order to allow above and other objects of the present invention, feature and advantage can
It is clearer and more comprehensible, the followings are specific embodiments of the present invention.
Detailed description of the invention
By reading the following detailed description of the preferred embodiment, various other advantages and benefits are common for this field
Technical staff will become clear.The drawings are only for the purpose of illustrating a preferred embodiment, and is not considered as to the present invention
Limitation.And throughout the drawings, the same reference numbers will be used to refer to the same parts.In the accompanying drawings:
Fig. 1 is a kind of process of control method that organic liquid waste is handled using supercritical water oxidation of the embodiment of the present invention
Figure;
Fig. 2 is a kind of structural frames of control system that organic liquid waste is handled using supercritical water oxidation of the embodiment of the present invention
Figure;
Fig. 3 is the schematic diagram of the control equipment of the embodiment of the present invention.
Specific embodiment
Exemplary embodiments of the present disclosure are described in more detail below with reference to accompanying drawings.Although showing the disclosure in attached drawing
Exemplary embodiment, it being understood, however, that may be realized in various forms the disclosure without should be by embodiments set forth here
It is limited.On the contrary, these embodiments are provided to facilitate a more thoroughly understanding of the present invention, and can be by the scope of the present disclosure
It is fully disclosed to those skilled in the art.
Those skilled in the art of the present technique are appreciated that unless otherwise defined, all terms used herein (including technology art
Language and scientific term), there is meaning identical with the general understanding of those of ordinary skill in fields of the present invention.Should also
Understand, those terms such as defined in the general dictionary, it should be understood that have in the context of the prior art
The consistent meaning of meaning, and unless otherwise will not be explained in an idealized or overly formal meaning by specific definitions.
Fig. 1 diagrammatically illustrates the controlling party using supercritical water oxidation processing organic liquid waste of one embodiment of the invention
The flow chart of method.Referring to Fig.1, the control method using supercritical water oxidation processing organic liquid waste of the embodiment of the present invention is specifically wrapped
Include following steps:
Step S11, the Current Temperatures and pressure of inside reactor conversion zone are monitored.
Step S12, the heating device of the reactor is controlled respectively according to the Current Temperatures of the conversion zone and pressure
And pressure-control valve, so that the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition, it is defeated
The organic liquid waste and hydrogen peroxide for being sent to inside reactor carry out supercritical water oxidation under current reaction condition.
Specifically, supercritical water oxidation condition is 650 DEG C, 25MPa.
In the present embodiment, when the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition
When, control dioxygen water pump is opened, and conveys hydrogen peroxide to inside reactor according to the corresponding initial setting flow of hydrogen peroxide;Work as institute
State conversion zone temperature and pressure keep stable state in predetermined time period after, control material-handling pump is opened, and is pressed
Organic liquid waste is conveyed to inside reactor according to the corresponding initial setting flow of material.
In a specific embodiment, it when equipment starts, first controls dioxygen water pump and opens, dioxygen water pump is conveyed, wait react
Device temperature, pressure reach supercriticality and are then turned on material-handling pump after stablizing, and convey organic waste to inside reactor
Liquid first stops material-handling pump when equipment stops, and gradually decreases dioxygen pump capacity until closing.
In the embodiment of the present invention, before the Current Temperatures of the monitoring inside reactor conversion zone and pressure, also wrap
Include following steps: the temperature of monitoring inside reactor preheated zone, the reactor include at least preheated zone and conversion zone;
When the temperature of the preheated zone reaches the first temperature threshold, it is defeated according to initial setting flow to control organic liquid waste and hydrogen peroxide
It is sent to the conversion zone of the reactor.
In the present embodiment, reactor guarantees high pressure by the check valve of feed inlet and the counterbalance valve in downstream, and linkage is arranged,
Outlet setting explosion venting valve;Reactor heating mode is infrared heating, and inlet and bringing-up section tail end are equipped with pressure gauge, preheating section and
Temperature measuring point is arranged in bringing-up section, to realize the monitoring to inside reactor preheated zone and conversion zone Current Temperatures and pressure;It is perpendicular
Formula reacts bottom of the tube setting precipitating salt outlet, and solid waste is discharged in not timing;Cooler is horizontal type jacket type structure, and exit is set
Set thermocouple temperature measurement point.
Specifically, the first temperature threshold of preheated zone can be set to 200 DEG C.In the present embodiment, organic liquid waste and double
Oxygen water is transported in supercritical water reaction device, is preheated by preheated zone, and reaction zone, flashing are entered after being preheated to 200 DEG C
Liquid feed flow is 2L/h, and hydrogen peroxide feed flow is 6~15L/h;In supercritical water reaction area, 650 DEG C, it is 25MPa, strong
Under oxidizing condition, scintillation solution molecule occur cracking, oxidation reaction and be converted into the reaction products such as carbon dioxide and water, realize it is inorganic
Change conversion.
Step S13, during supercritical water oxidation, it is gentle that control cooler cool down to the reactant of generation
Liquid separating treatment.
Specifically, control cooler handles the reactant of generation during supercritical water oxidation.Specifically
, reaction product passes through cooling (80 DEG C) again, gas-liquid separation is divided into gas and liquid, and gas is mainly carbon dioxide, liquid master
If water.
Step S14, TOC value, COD value and the pH value of liquid are generated after monitoring gas-liquid separation processing, and according to the TOC value
Or COD value adjusts the feed flow of the organic liquid waste and/or the temperature of the conversion zone.
Wherein, TOC is total content of organic carbon, and COD is COD.
In the present embodiment, cooling system is made of cooling arrangement, gas-liquid separator, outlet COD on-line measurement device.It is cold
But device device includes the compositions such as outlet cooler, deionized water feeder channel, deionized water circulating pump;Gas-liquid separator is that decompression is held
Device, after products stream depressurizes herein, gas and liquid are drained respectively, and liquid sampling analyzes total organic carbon and outlet COD value, are passed through
COD value feedback regulates and controls reaction.
Control method and system provided in an embodiment of the present invention using supercritical water oxidation processing organic liquid waste, the present invention
TOC value in reactant or COD value are carried out feedback with the feed flow of organic liquid waste to be associated with, pass through TOC value or COD value feedback pair
Reaction is regulated and controled, and is accelerated reaction speed, is reduced the reaction time, so that fully reacting, secondary amount of waste is few, clean environment is friendly
It is good.
In embodiments of the present invention, the feed flow that the organic liquid waste is adjusted according to the TOC value or COD value
And/or the temperature of the conversion zone, it specifically includes: when the COD value is greater than the first COD feedback threshold, having described in reduction
The feed flow of machine waste liquid, and the heating device of the reactor is opened, so that the temperature of the conversion zone is maintained at 650 DEG C
More than;Or, reducing the feed flow of the organic liquid waste, and open institute when the TOC value is greater than the first TOC feedback threshold
The heating device of reactor is stated, so that the temperature of the conversion zone is maintained at 650 DEG C or more.
Further, when the COD value is less than the 2nd COD feedback threshold, restore the initial setting of the organic liquid waste
Flow, closes the heating device of the reactor, and the 2nd COD feedback threshold is less than the first COD feedback threshold;Or,
When the TOC value is less than the 2nd TOC feedback threshold, restores the initial setting flow of the organic liquid waste, close the reaction
The heating device of device, the 2nd TOC feedback threshold are less than the first TOC feedback threshold.
In an embodiment of the invention, can according to COD value adjust organic liquid waste feed flow and/or the reaction
The temperature in region further includes steps of when the COD value is greater than the first COD feedback threshold, reduces the organic waste
The feed flow of liquid, and open the heating device of the reactor so that the temperature of the conversion zone be maintained at 650 DEG C with
On.When the COD value is less than the 2nd COD feedback threshold, restore the initial setting flow of the organic liquid waste, closes described anti-
The heating device of device is answered, the 2nd COD feedback threshold is less than the first COD feedback threshold.
Wherein, the specific value of the first COD feedback threshold and the 2nd COD feedback threshold can be configured by user.
Wherein, infrared heating can be used in the heating device of reactor, without introducing combustion adjuvant starting technique.
In the embodiment of the present invention, control system uses linkage control, feeds back temperature using on-line monitoring cooler outlet COD value
Degree and flow reduce organic matter feed rate when COD value is greater than 150-250mg/L, and opening infrared heating makes equipment stablize fortune
Row when COD value is less than 100mg/L, that is, meets integrated wastewater discharge standard GB8978-1996, restores at this time at 650 DEG C or more
Organic matter feed rate closes infrared heating and real-time monitoring.
In another embodiment of the present invention, feed flow and/or the institute that the organic liquid waste is adjusted according to the TOC value
The temperature for stating conversion zone is further included steps of when the TOC value is greater than the first TOC feedback threshold, described in reduction
The feed flow of organic liquid waste, and the heating device of the reactor is opened, so that the temperature of the conversion zone is maintained at 650
DEG C or more.Further, when the TOC value is less than the 2nd TOC feedback threshold, restore the initial setting stream of the organic liquid waste
Amount, closes the heating device of the reactor, and the 2nd TOC feedback threshold is less than the first TOC feedback threshold.
Wherein, the specific value of the first TOC feedback threshold and the 2nd TOC feedback threshold can be configured by user, this hair
It is bright not illustrate.
For embodiment of the method, for simple description, therefore, it is stated as a series of action combinations, but this field
Technical staff should be aware of, and embodiment of that present invention are not limited by the describe sequence of actions, because implementing according to the present invention
Example, some steps may be performed in other sequences or simultaneously.Secondly, those skilled in the art should also know that, specification
Described in embodiment belong to preferred embodiment, the actions involved are not necessarily necessary for embodiments of the present invention.
Fig. 2 diagrammatically illustrates the control system using supercritical water oxidation processing organic liquid waste of one embodiment of the invention
The structural schematic diagram of system.Referring to Fig. 2, the control system using supercritical water oxidation processing organic liquid waste of the embodiment of the present invention has
Body includes the first monitoring modular 201, reaction controlling module 202, cooling control module 203 and feedback control module 204,
In:
First monitoring modular 201, for monitoring the Current Temperatures and pressure of inside reactor conversion zone;
Reaction controlling module 202, for controlling the reaction respectively according to the Current Temperatures and pressure of the conversion zone
The heating device and pressure-control valve of device, so that the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation
Reaction condition, it is anti-that the organic liquid waste and hydrogen peroxide for being transported to inside reactor carry out supercritical water oxidation under current reaction condition
It answers;
Cooling control module 203, for during supercritical water oxidation, controlling cooler to the reactant of generation
Carry out cooling and gas-liquid separating treatment;
Feedback control module 204, for monitoring the TOC value, COD value and the pH value that generate liquid after gas-liquid separation is handled, and
The feed flow of the organic liquid waste and/or the temperature of the conversion zone are adjusted according to the TOC value or COD value.
In embodiments of the present invention, the system also includes attached second monitoring modulars not shown in the figure and charging control mould
Block, in which:
Second monitoring modular, in the first monitoring module monitors inside reactor conversion zone Current Temperatures and
Before pressure, the temperature of inside reactor preheated zone is monitored, the reactor includes at least preheated zone and conversion zone;
Control module is fed, for controlling organic liquid waste when the temperature of the preheated zone reaches the first temperature threshold
The conversion zone of the reactor is transported to according to initial setting flow with hydrogen peroxide.
In embodiments of the present invention, the feedback control module is specifically used for feeding back when the COD value greater than the first COD
When threshold value, the feed flow of the organic liquid waste is reduced, and opens the heating device of the reactor, so that the conversion zone
Temperature be maintained at 650 DEG C or more, when the COD value is less than the 2nd COD feedback threshold, restore the initial of the organic liquid waste
Flow is set, the heating device of the reactor is closed, the 2nd COD feedback threshold is less than the first COD feedback threshold;
In an alternative embodiment of the invention, the feedback control module is specifically also used to be greater than first when the TOC value
When TOC feedback threshold, the feed flow of the organic liquid waste is reduced, and opens the heating device of the reactor, so that described
The temperature of conversion zone is maintained at 650 DEG C or more, when the TOC value is less than the 2nd TOC feedback threshold, restores the organic waste
The initial setting flow of liquid, closes the heating device of the reactor, and the 2nd TOC feedback threshold is less than the first TOC
Feedback threshold.
In the embodiment of the present invention, control module 202 is fed, it is full specifically for the temperature and pressure when the conversion zone
When the preset supercritical water oxidation condition of foot, control dioxygen water pump is opened, and is flowed according to the corresponding initial setting of hydrogen peroxide
It measures to inside reactor and conveys hydrogen peroxide;When the temperature and pressure of the conversion zone keeps stablizing shape in predetermined time period
After state, control material-handling pump is opened, and conveys organic liquid waste to inside reactor according to the corresponding initial setting flow of material.
The charging control module 202 is specifically also used to when the apparatus is shut, first stop material-handling pump, and gradually drop
Low dioxygen pump capacity is until close.
For system embodiments, since it is basically similar to the method embodiment, related so being described relatively simple
Place illustrates referring to the part of embodiment of the method.
System embodiment described above is only schematical, wherein described, unit can as illustrated by the separation member
It is physically separated with being or may not be, component shown as a unit may or may not be physics list
Member, it can it is in one place, or may be distributed over multiple network units.It can be selected according to the actual needs
In some or all of the modules achieve the purpose of the solution of this embodiment.Those of ordinary skill in the art are not paying creativeness
Labour in the case where, it can understand and implement.
Control method and system provided in an embodiment of the present invention using supercritical water oxidation processing organic liquid waste, the present invention
COD value in reactant is carried out feedback with the feed flow of organic liquid waste to be associated with, reaction is regulated and controled by COD value feedback,
It accelerates reaction speed, reduce the reaction time, so that fully reacting, secondary amount of waste is few, clean environment is friendly.
In addition, it is stored thereon with computer program the embodiment of the invention also provides a kind of computer readable storage medium,
The step of program realizes method as described above when being executed by processor.
In the present embodiment, module/unit of the control system integration using supercritical water oxidation processing organic liquid waste
If be realized in the form of SFU software functional unit and when sold or used as an independent product, can store in a computer
In read/write memory medium.Based on this understanding, the present invention realizes all or part of the process in above-described embodiment method,
Relevant hardware can be instructed to complete by computer program, it is computer-readable that the computer program can be stored in one
In storage medium, the computer program is when being executed by processor, it can be achieved that the step of above-mentioned each embodiment of the method.Wherein,
The computer program includes computer program code, and the computer program code can be source code form, object identification code
Form, executable file or certain intermediate forms etc..The computer-readable medium may include: that can carry the computer
Any entity or device of program code, USB flash disk, mobile hard disk, magnetic disk, CD, computer storage, read-only are deposited at recording medium
Reservoir (ROM, Read-Only Memory), random access memory (RAM, Random Access Memory), electric carrier wave letter
Number, telecommunication signal and software distribution medium etc..It should be noted that the content that the computer-readable medium includes can root
Increase and decrease appropriate is carried out according to the requirement made laws in jurisdiction with patent practice, such as in certain jurisdictions, according to vertical
Method and patent practice, computer-readable medium do not include electric carrier signal and telecommunication signal.
Fig. 3 is the schematic diagram of control equipment provided in an embodiment of the present invention.Control equipment provided in an embodiment of the present invention, packet
It includes memory 301, processor 302 and is stored in the computer program that can be run on memory 301 and on processor 302, institute
It states and realizes above-mentioned each control using supercritical water oxidation processing organic liquid waste when processor 302 executes the computer program
Step in embodiment of the method, such as step S11 shown in FIG. 1, the Current Temperatures and pressure that monitor inside reactor conversion zone
Power.Step S12, the heating device and pressure of the reactor are controlled respectively according to the Current Temperatures of the conversion zone and pressure
Control valve is transported to anti-so that the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition
Organic liquid waste and hydrogen peroxide inside device is answered to carry out supercritical water oxidation under current reaction condition.Step S13, face super
In boundary's water oxidation reaction process, control cooler carries out cooling and gas-liquid separating treatment to the reactant of generation.Step S14, it supervises
TOC value, COD value and the pH value of liquid are generated after surveying gas-liquid separation processing, and is had according to the TOC value or COD value adjustment
The temperature of the feed flow of machine waste liquid and/or the conversion zone.Alternatively, the processor 302 executes the computer program
The function of each module/unit in the above-mentioned each control system embodiment using supercritical water oxidation processing organic liquid waste of Shi Shixian,
Such as the first monitoring modular 201 shown in Fig. 2, reaction controlling module 202, cooling control module 203 and feedback control module
204。
Illustratively, the computer program can be divided into one or more module/units, one or more
A module/unit is stored in the memory, and is executed by the processor, to complete the present invention.It is one or more
A module/unit can be the series of computation machine program instruction section that can complete specific function, and the instruction segment is for describing institute
State implementation procedure of the computer program in the control system using supercritical water oxidation processing organic liquid waste.For example, institute
The first monitoring modular 201, reaction controlling module 202, cooling control module 203 and anti-can be divided by stating computer program
Present control module 204.
The control equipment can be desktop PC, notebook, palm PC and cloud server etc. and calculate equipment.
The control equipment may include, but be not limited only to, processor, memory.It will be understood by those skilled in the art that the schematic diagram
3 be only the example for controlling equipment, does not constitute the restriction to control equipment, may include than illustrating more or fewer portions
Part perhaps combines certain components or different components, such as the control equipment can also include input-output equipment, net
Network access device, bus etc..
The processor can be central processing unit (Central Processing Unit, CPU), can also be it
His general processor, digital signal processor (Digital Signal Processor, DSP), specific integrated circuit
(Application Specific Integrated Circuit, ASIC), ready-made programmable gate array (Field-
Programmable Gate Array, FPGA) either other programmable logic device, discrete gate or transistor logic,
Discrete hardware components etc..General processor can be microprocessor or the processor is also possible to any conventional processor
It is the control centre of the control equipment Deng, the processor, entirely controls each of equipment using various interfaces and connection
A part.
The memory can be used for storing the computer program and/or module, and the processor is by operation or executes
Computer program in the memory and/or module are stored, and calls the data being stored in memory, described in realization
Control the various functions of equipment.The memory can mainly include storing program area and storage data area, wherein storing program area
It can application program (such as sound-playing function, image player function etc.) needed for storage program area, at least one function etc.;
Storage data area, which can be stored, uses created data (such as audio data, phone directory etc.) etc. according to mobile phone.In addition, storage
Device may include high-speed random access memory, can also be hard including nonvolatile memory, such as hard disk, memory, plug-in type
Disk, intelligent memory card (Smart Media Card, SMC), secure digital (Secure Digital, SD) card, flash card
(Flash Card), at least one disk memory, flush memory device or other volatile solid-state parts.
It will be appreciated by those of skill in the art that although some embodiments in this include included in other embodiments
Certain features rather than other feature, but the combination of the feature of different embodiments means to be within the scope of the present invention simultaneously
And form different embodiments.For example, in the following claims, the one of any of embodiment claimed all may be used
Come in a manner of in any combination using.
Finally, it should be noted that the above embodiments are merely illustrative of the technical solutions of the present invention, rather than its limitations;Although
Present invention has been described in detail with reference to the aforementioned embodiments, those skilled in the art should understand that: it still may be used
To modify the technical solutions described in the foregoing embodiments or equivalent replacement of some of the technical features;
And these are modified or replaceed, technical solution of various embodiments of the present invention that it does not separate the essence of the corresponding technical solution spirit and
Range.
Claims (10)
1. a kind of control method using supercritical water oxidation processing organic liquid waste characterized by comprising
Monitor the Current Temperatures and pressure of inside reactor conversion zone;
Control the heating device and pressure-control valve of the reactor respectively according to the Current Temperatures of the conversion zone and pressure,
So that the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition, it is transported to inside reactor
Organic liquid waste and hydrogen peroxide supercritical water oxidation is carried out under current reaction condition;
During supercritical water oxidation, control cooler carries out cooling and gas-liquid separating treatment to the reactant of generation;
TOC value, COD value and the pH value of liquid are generated after monitoring gas-liquid separation processing, and is adjusted according to the TOC value or COD value
The temperature of the feed flow of the organic liquid waste and/or the conversion zone.
2. the method according to claim 1, wherein in the current temperature of the monitoring inside reactor conversion zone
Before degree and pressure, the method also includes:
The temperature of inside reactor preheated zone is monitored, the reactor includes at least preheated zone and conversion zone;
When the temperature of the preheated zone reaches the first temperature threshold, organic liquid waste and hydrogen peroxide are controlled according to initial setting stream
Amount is transported to the conversion zone of the reactor.
3. method according to claim 1 or 2, which is characterized in that described according to the TOC value or COD value adjustment
The temperature of the feed flow of organic liquid waste and/or the conversion zone, comprising:
When the COD value is greater than the first COD feedback threshold, the feed flow of the organic liquid waste is reduced, and is opened described anti-
The heating device of device is answered, so that the temperature of the conversion zone is maintained at 650 DEG C or more;
Or,
When the TOC value is greater than the first TOC feedback threshold, the feed flow of the organic liquid waste is reduced, and is opened described anti-
The heating device of device is answered, so that the temperature of the conversion zone is maintained at 650 DEG C or more.
4. according to the method described in claim 3, it is characterized in that, the method also includes:
When the COD value is less than the 2nd COD feedback threshold, restore the initial setting flow of the organic liquid waste, described in closing
The heating device of reactor, the 2nd COD feedback threshold are less than the first COD feedback threshold;
Or,
When the TOC value is less than the 2nd TOC feedback threshold, restore the initial setting flow of the organic liquid waste, described in closing
The heating device of reactor, the 2nd TOC feedback threshold are less than the first TOC feedback threshold.
5. the method according to claim 1, wherein described when the temperature and pressure of the conversion zone is all satisfied
When preset supercritical water oxidation condition, according to the conveying of initial setting flow control organic liquid waste and hydrogen peroxide, comprising:
When the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation condition, dioxygen water pump is controlled
It opens, and conveys hydrogen peroxide to inside reactor according to the corresponding initial setting flow of hydrogen peroxide;
After the temperature and pressure of the conversion zone keeps stable state in predetermined time period, control material-handling pump is opened
It opens, and conveys organic liquid waste to inside reactor according to the corresponding initial setting flow of material.
6. a kind of control system using supercritical water oxidation processing organic liquid waste characterized by comprising
First monitoring modular, for monitoring the Current Temperatures and pressure of inside reactor conversion zone;
Reaction controlling module controls the heating of the reactor for the Current Temperatures and pressure according to the conversion zone respectively
Device and pressure-control valve, so that the temperature and pressure of the conversion zone is all satisfied preset supercritical water oxidation item
Part, the organic liquid waste and hydrogen peroxide for being transported to inside reactor carry out supercritical water oxidation under current reaction condition;
Cooling control module, for during supercritical water oxidation, control cooler to carry out the reactant of generation cold
But with gas-liquid separating treatment;
Feedback control module, for monitoring the TOC value, COD value and the pH value that generate liquid after gas-liquid separation is handled, and according to described
TOC value or COD value adjust the feed flow of the organic liquid waste and/or the temperature of the conversion zone.
7. system according to claim 6, which is characterized in that the system also includes:
Second monitoring modular, for the Current Temperatures and pressure in the first monitoring module monitors inside reactor conversion zone
Before, the temperature of inside reactor preheated zone is monitored, the reactor includes at least preheated zone and conversion zone;
Control module is fed, for when the temperature of the preheated zone reaches the first temperature threshold, control organic liquid waste and double
Oxygen water is transported to the conversion zone of the reactor according to initial setting flow.
8. system according to claim 6 or 7, which is characterized in that the feedback control module is specifically used for when described
When COD value is greater than the first COD feedback threshold, the feed flow of the organic liquid waste is reduced, and open the heating of the reactor
Device, so that the temperature of the conversion zone is maintained at 650 DEG C or more, when the COD value is less than the 2nd COD feedback threshold,
The initial setting flow for restoring the organic liquid waste, closes the heating device of the reactor, and the 2nd COD feedback threshold is small
In the first COD feedback threshold;
Or,
When the TOC value is greater than the first TOC feedback threshold, the feed flow of the organic liquid waste is reduced, and is opened described anti-
The heating device of device is answered, so that the temperature of the conversion zone is maintained at 650 DEG C or more, when the TOC value is anti-less than the 2nd TOC
When presenting threshold value, restores the initial setting flow of the organic liquid waste, close the heating device of the reactor, the 2nd TOC
Feedback threshold is less than the first TOC feedback threshold.
9. a kind of computer readable storage medium, is stored thereon with computer program, which is characterized in that the program is held by processor
It is realized when row such as the step of any one of claim 1-5 the method.
10. a kind of control equipment including memory, processor and stores the calculating that can be run on a memory and on a processor
Machine program, which is characterized in that the processor realizes the step such as any one of claim 1-5 the method when executing described program
Suddenly.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910093699.3A CN109650517A (en) | 2019-01-30 | 2019-01-30 | Utilize the control method and system of supercritical water oxidation processing organic liquid waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910093699.3A CN109650517A (en) | 2019-01-30 | 2019-01-30 | Utilize the control method and system of supercritical water oxidation processing organic liquid waste |
Publications (1)
Publication Number | Publication Date |
---|---|
CN109650517A true CN109650517A (en) | 2019-04-19 |
Family
ID=66121781
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910093699.3A Pending CN109650517A (en) | 2019-01-30 | 2019-01-30 | Utilize the control method and system of supercritical water oxidation processing organic liquid waste |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109650517A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113173635A (en) * | 2021-03-17 | 2021-07-27 | 海湾环境科技(北京)股份有限公司 | Supercritical water oxidation reaction device |
CN115974257A (en) * | 2023-01-09 | 2023-04-18 | 青岛科技大学 | Supercritical water oxidation self-adaptive treatment technology for high-concentration TNT explosive wastewater |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101418376A (en) * | 2008-11-27 | 2009-04-29 | 东华大学 | A kind of method and apparatus of beneficiation and metallurgy of refractory gold ore by supercritical water oxidation |
CN101544419A (en) * | 2008-03-27 | 2009-09-30 | 楼龙春 | Method and device for oxidizing and treating sewage or sludge containing organic substances by supercritical water |
WO2012129202A1 (en) * | 2011-03-22 | 2012-09-27 | Alstom Technology Ltd | Real-time control method and gas purification system for solvent based capture systems |
CN103157405A (en) * | 2011-12-15 | 2013-06-19 | 株式会社理光 | Liquid waste treatment apparatus |
CN104709998A (en) * | 2015-03-23 | 2015-06-17 | 内蒙古天一环境技术有限公司 | Small-size supercritical water oxidation reaction system and control method thereof |
-
2019
- 2019-01-30 CN CN201910093699.3A patent/CN109650517A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101544419A (en) * | 2008-03-27 | 2009-09-30 | 楼龙春 | Method and device for oxidizing and treating sewage or sludge containing organic substances by supercritical water |
CN101418376A (en) * | 2008-11-27 | 2009-04-29 | 东华大学 | A kind of method and apparatus of beneficiation and metallurgy of refractory gold ore by supercritical water oxidation |
WO2012129202A1 (en) * | 2011-03-22 | 2012-09-27 | Alstom Technology Ltd | Real-time control method and gas purification system for solvent based capture systems |
CN103157405A (en) * | 2011-12-15 | 2013-06-19 | 株式会社理光 | Liquid waste treatment apparatus |
CN104709998A (en) * | 2015-03-23 | 2015-06-17 | 内蒙古天一环境技术有限公司 | Small-size supercritical water oxidation reaction system and control method thereof |
Non-Patent Citations (1)
Title |
---|
王齐: "超临界水氧化处理印染废水实验研究", 《中国博士学位论文全文数据库 工程科技Ⅰ辑》 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113173635A (en) * | 2021-03-17 | 2021-07-27 | 海湾环境科技(北京)股份有限公司 | Supercritical water oxidation reaction device |
CN115974257A (en) * | 2023-01-09 | 2023-04-18 | 青岛科技大学 | Supercritical water oxidation self-adaptive treatment technology for high-concentration TNT explosive wastewater |
CN115974257B (en) * | 2023-01-09 | 2024-03-08 | 青岛科技大学 | Supercritical water oxidation self-adaptive treatment method for high-concentration TNT explosive wastewater |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN109650517A (en) | Utilize the control method and system of supercritical water oxidation processing organic liquid waste | |
Ojeda et al. | Puberty in the rat | |
SG160392A1 (en) | Control system method and apparatus for continuous liquid phase hydroprocessing | |
CN111243978B (en) | Semiconductor processing apparatus and semiconductor processing method | |
CN103080015B (en) | Removing dissolved gases in the make up water of nuclear reactor | |
US20100254871A1 (en) | Aqueous phase oxidation process | |
Tayyebi et al. | A new approach of GA-based type reduction of interval type-2 fuzzy model for nonlinear MIMO system: Application in methane oxidation process | |
Mucha et al. | Analysis of wet oxidation process after initial thermohydrolysis of excess sewage sludge | |
US7951988B2 (en) | Aqueous phase oxidation process | |
Raisanen et al. | A reaction mechanism for plasma electrolysis of AgNO3 forming silver nanoclusters and nanoparticles | |
US8115047B2 (en) | Aqueous phase oxidation process | |
US8168847B2 (en) | Aqueous phase oxidation process | |
US7915474B2 (en) | Aqueous phase oxidation process | |
CN204656494U (en) | A kind of industrial mass stablizes the shunting means preparing quantum dot | |
JP2003236570A (en) | Method and apparatus for hydrothermal reaction | |
CN105344292A (en) | Supercritical water oxidation process control method and control system | |
CN204656495U (en) | A kind of industrial mass stablizes the tandem arrangement preparing quantum dot | |
Tan et al. | Exploring the role of eRNA in regulating gene expression | |
JP2003236393A (en) | Catalyst reduction method | |
Afsahi et al. | Complex reactions sensitivity to different factors: Numerical investigation of MoS2 reduction by hydrogen in lime presence | |
Wang et al. | Study of predicting combined chaotic time series using neural networks | |
Kotsiopoulos et al. | A dynamic analysis of chalcopyrite bioleaching in continuous flow reactor systems | |
Reichenbach et al. | Stochastic effects on biodiversity in cyclic coevolutionary dynamics | |
Lin et al. | Development of a first generation perfusion process and medium for continuous processing based on existing fed-batch platform media | |
Gandham et al. | Management of Biochemical Recurrence After Prostatectomy Within the MUSIC Collaborative |
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 | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190419 |