[go: up one dir, main page]
More Web Proxy on the site http://driver.im/

CN110422926A - A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system - Google Patents

A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system Download PDF

Info

Publication number
CN110422926A
CN110422926A CN201810769357.4A CN201810769357A CN110422926A CN 110422926 A CN110422926 A CN 110422926A CN 201810769357 A CN201810769357 A CN 201810769357A CN 110422926 A CN110422926 A CN 110422926A
Authority
CN
China
Prior art keywords
oxygen
micro
aeration tank
wei yang
aeration
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
CN201810769357.4A
Other languages
Chinese (zh)
Inventor
不公告发明人
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.)
Jiangsu Prande Energy Saving Technology Co Ltd
Original Assignee
Jiangsu Prande Energy Saving 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 Jiangsu Prande Energy Saving Technology Co Ltd filed Critical Jiangsu Prande Energy Saving Technology Co Ltd
Priority to CN201810769357.4A priority Critical patent/CN110422926A/en
Publication of CN110422926A publication Critical patent/CN110422926A/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
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/2846Anaerobic digestion processes using upflow anaerobic sludge blanket [UASB] reactors
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/302Nitrification and denitrification treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/20Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
    • 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
    • C02F2209/02Temperature
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/14NH3-N
    • 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
    • C02F2209/22O2
    • 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
    • C02F2209/40Liquid flow rate
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Activated Sludge Processes (AREA)

Abstract

The present invention provides a kind of biogas slurries to nitrify denitrogenation reuse autocontrol method, it is characterised in that: biogas slurry nitrification denitrogenation reuse autocontrol method includes: temperature, oxygen content and the pH value monitored in UASB reactor and is adjusted;It the flow of biogas slurry and waste water of livestock poultry raw water and is adjusted or alarms in monitoring turbid water system;The micro- oxygen aeration tank of monitoring No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang are simultaneously adjusted;The flow of the mixed liquor of monitoring No.1 micro- oxygen aeration tank institute received No. three aeration tanks Wei Yang generation is simultaneously adjusted or alarms.Controling system integration degree of the invention is high, and the present invention will be fused in single system the control of all components and carry out, and system can be according to all data, the reason of some parameter drift-out normal value of comprehensive analysis, to obtain more accurate control command.System of the invention simultaneously is more simplified compared with the prior art, and treatment effeciency is higher.

Description

A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system
Technical field
The present invention relates to technical field of anaerobic fermentation, nitrify denitrogenation reuse automatic control side especially with regard to a kind of biogas slurry Method and system.
Background technique
The mode that China's large-scale pig farm generallys use anaerobic methane production carries out recovery energy and processing to breeding wastewater.So And the biogas slurry that pig farm breeding wastewater is generated through Anaerobic Treatment be a kind of high organic matter, high ammonia nitrogen, low COD/TN ratio (C/N < 5) it is useless Water has the characteristics that yield is big, pollutant concentration is high, environmental pollution is serious, and efficient low-consume simultaneous denitrification is to realize it except carbon The ideal outlet of prevention and cure of pollution.Conventional denitrification denitrification process usually by denitrifying bacterium consumption carbon source completed, but it is too low into Water C/N ratio will lead to nitric efficiency decline, and TN cannot achieve qualified discharge.And piggery wastewater raw water contains sufficient organic carbon Source takes the mode of raw water substep water inlet to be conducive to improve water inlet C/N ratio, realizes carbon source, basicity self-balancing, improves denitrogenation effect Fruit.With the appearance of " livestock and poultry breeding industry pollution discharge standard " (secondary exposure draft), livestock breeding wastewater discharge mark Brigadier is promoted to 150 mg/L of COD, 40 mg/L of ammonia nitrogen, 70 mg/L of total nitrogen and 5 mg/L of total phosphorus (TP).Nevertheless, I The treatment process of the existing large-scale pig farm waste water of state is mainly " anaerobic methane production .A/O " group technology, the high oxyty of aerobic section (mg/L of DO > 2) will necessarily bring huge energy loss, the up to 40%-50% of total energy consumption.Meanwhile by the low C/ of anaerobism biogas slurry N-bit influences, and A/O sections of denitrifying carbon sources are insufficient, and basicity is unbalance, and Process for Effluent COD, TN, TP concentration is unable to reach two substantially The emission request of secondary exposure draft.
The information disclosed in the background technology section is intended only to increase the understanding to general background of the invention, without answering When being considered as recognizing or imply that the information constitutes the prior art already known to those of ordinary skill in the art in any form.
Summary of the invention
The purpose of the present invention is to provide a kind of biogas slurry nitrification denitrogenation reuse autocontrol method and systems, can overcome The shortcomings that prior art.
To achieve the above object, the present invention provides a kind of biogas slurries to nitrify denitrogenation reuse autocontrol method, and feature exists In: biogas slurry nitrification denitrogenation reuse autocontrol method includes:
Monitor temperature, oxygen content and the pH value in UASB reactor;
If temperature, oxygen content in UASB reactor and one or more deviation first predetermined value set in pH value, One or more in temperature, oxygen content and pH value in UASB reactor are adjusted;
Monitor the flow of biogas slurry and waste water of livestock poultry raw water in turbid water system, wherein biogas slurry is the product of UASB reactor;
If the ratio between flow of biogas slurry and waste water of livestock poultry raw water deviates second predetermined value in turbid water system, turbid water system is carried out Diagnosis, if it find that turbid water system water inlet blocks, then issues warning message, if not finding turbid water system failure, Then adjust the flow of biogas slurry Yu waste water of livestock poultry raw water;
Monitor the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And ammonia nitrogen concentration;
If the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And one or more deviation second predetermined value set in ammonia nitrogen concentration, then to the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang And one or more in dissolved oxygen concentration, pH value and the ammonia nitrogen concentration in No. three aeration tanks Wei Yang are adjusted;
Monitor the flow of the mixed liquor of No.1 micro- oxygen aeration tank institute received No. three aeration tanks Wei Yang generation;If the stream of mixed liquor Amount deviates the 4th predetermined value, then diagnoses to No. three aeration tanks Wei Yang, if it find that No. three aeration tank Wei Yang water routes occur to block up Plug, then issue the second warning message, if not finding No. three aeration tank Wei Yang failures, the flow of mixed liquor.
In a preferred embodiment, if temperature, oxygen content in UASB reactor and one in pH value or Multinomial deviation first predetermined value set, then in temperature, oxygen content and the pH value in UASB reactor it is one or more into Row adjustment specifically includes:
If temperature in UASB reactor is lower than UASB reactor predetermined temperature, control heating device to UASB reactor into Row heating;
If the oxygen content in UASB reactor is higher than UASB reactor oxygen content predetermined concentration, controls and open aspiration pump progress Pumping.
In a preferred embodiment, if the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three micro- oxygen expose Dissolved oxygen concentration, pH value in gas pond and one or more deviation second predetermined value set in ammonia nitrogen concentration, then to No.1 In micro- oxygen aeration tank, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang One or more be adjusted include the following steps:
If any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is molten It solves oxygen concentration and is lower than micro- predetermined dissolved oxygen concentration in oxygen aeration tank, then control oxygen generator and be oxygenated to micro- oxygen aeration tank;
If the pH of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Value is lower than micro- predetermined pH value in oxygen aeration tank, then controls lye Chi Xiangwei oxygen aeration tank addition lye;
If the ammonia of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Nitrogen concentration is lower than micro- predetermined ammonia nitrogen concentration in oxygen aeration tank, then controls heating device and improve heating power.
In a preferred embodiment, wherein dense for micro- predetermined dissolved oxygen in oxygen aeration tank of the micro- oxygen aeration tank of No.1 Degree is 0.1-0.2mg/L, and micro- predetermined dissolved oxygen concentration in oxygen aeration tank for No. two aeration tanks Wei Yang is 0.05-0.1mg/L, needle Micro- predetermined dissolved oxygen concentration in oxygen aeration tank to No. three aeration tanks Wei Yang is 0-0.05mg/L.
In a preferred embodiment, if it find that turbid water system water inlet blocks, then warning message tool is issued Body are as follows: via cordless communication network, send warning message to wireless terminal;
Wherein, if it find that No. three aeration tanks Wei Yang water route blocks, then the second warning message is issued specifically: via wireless Communication network sends the second warning message to wireless terminal.
The present invention provides a kind of biogas slurries to nitrify denitrogenation reuse automatic control system, it is characterised in that: biogas slurry nitrifies denitrogenation Reuse automatic control system includes:
UASB reactor monitors control module, is configured as:
Monitor temperature, oxygen content and the pH value in UASB reactor;
If temperature, oxygen content in UASB reactor and one or more deviation first predetermined value set in pH value, One or more in temperature, oxygen content and pH value in UASB reactor are adjusted;
Turbid water system monitors control module, is configured as:
Monitor the flow of biogas slurry and waste water of livestock poultry raw water in turbid water system, wherein biogas slurry is the product of UASB reactor;
If the ratio between flow of biogas slurry and waste water of livestock poultry raw water deviates second predetermined value in turbid water system, turbid water system is carried out Diagnosis, if it find that turbid water system water inlet blocks, then issues warning message, if not finding turbid water system failure, Then adjust the flow of biogas slurry Yu waste water of livestock poultry raw water;
Multiple micro- oxygen aeration tanks monitor control module, are configured as:
Monitor the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And ammonia nitrogen concentration;
If the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And one or more deviation second predetermined value set in ammonia nitrogen concentration, then to the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang And one or more in dissolved oxygen concentration, pH value and the ammonia nitrogen concentration in No. three aeration tanks Wei Yang are adjusted;
Monitor the flow of the mixed liquor of No.1 micro- oxygen aeration tank institute received No. three aeration tanks Wei Yang generation;If the stream of mixed liquor Amount deviates the 4th predetermined value, then diagnoses to No. three aeration tanks Wei Yang, if it find that No. three aeration tank Wei Yang water routes occur to block up Plug, then issue the second warning message, if not finding No. three aeration tank Wei Yang failures, the flow of mixed liquor.
In a preferred embodiment, if temperature, oxygen content in UASB reactor and one in pH value or Multinomial deviation first predetermined value set, then in temperature, oxygen content and the pH value in UASB reactor it is one or more into Row adjustment specifically includes:
If temperature in UASB reactor is lower than UASB reactor predetermined temperature, control heating device to UASB reactor into Row heating;
If the oxygen content in UASB reactor is higher than UASB reactor oxygen content predetermined concentration, controls and open aspiration pump progress Pumping.
In a preferred embodiment, if the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three micro- oxygen expose Dissolved oxygen concentration, pH value in gas pond and one or more deviation second predetermined value set in ammonia nitrogen concentration, then to No.1 In micro- oxygen aeration tank, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang One or more be adjusted include the following steps:
If any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is molten It solves oxygen concentration and is lower than micro- predetermined dissolved oxygen concentration in oxygen aeration tank, then control oxygen generator and be oxygenated to micro- oxygen aeration tank;
If the pH of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Value is lower than micro- predetermined pH value in oxygen aeration tank, then controls lye Chi Xiangwei oxygen aeration tank addition lye;
If the ammonia of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Nitrogen concentration is lower than micro- predetermined ammonia nitrogen concentration in oxygen aeration tank, then controls heating device and improve heating power.
In a preferred embodiment, wherein dense for micro- predetermined dissolved oxygen in oxygen aeration tank of the micro- oxygen aeration tank of No.1 Degree is 0.1-0.2mg/L, and micro- predetermined dissolved oxygen concentration in oxygen aeration tank for No. two aeration tanks Wei Yang is 0.05-0.1mg/L, needle Micro- predetermined dissolved oxygen concentration in oxygen aeration tank to No. three aeration tanks Wei Yang is 0-0.05mg/L.
In a preferred embodiment, if it find that turbid water system water inlet blocks, then warning message tool is issued Body are as follows: via cordless communication network, send warning message to wireless terminal;
Wherein, if it find that No. three aeration tanks Wei Yang water route blocks, then the second warning message is issued specifically: via wireless Communication network sends the second warning message to wireless terminal.
Compared with prior art, the present invention has the advantage that currently available technology (such as CN105541008B) Propose some removal of carbon and nitrogen treatment process, the generally existing following problem of removal of carbon and nitrogen technique in the prior art: 1, system collection It is lower at degree, for each processing stage using the method that controls respectively control namely system in for aeration tank Control system be the more set systems being separated from each other for the control system of sedimentation basin, this may cause several sets in control process System interferes with each other, and makes entirely different control instruction;2, system complex causes system to be deposited due to the backwardness of control technology In redundancy, lead to the decline of system treatment efficiency.For problem of the prior art, the present invention develops a kind of novel denitrogenation system The autocontrol method of system.Controling system integration degree of the invention is high, and the present invention will be fused to the control of all components Carried out in single system, system can according to all data, the reason of some parameter drift-out normal value of comprehensive analysis, thus To more accurate control command.System of the invention simultaneously is more simplified compared with the prior art, and treatment effeciency is higher.
Detailed description of the invention
Fig. 1 is method flow diagram according to an embodiment of the present invention.
Fig. 2 is the block diagram of control system according to an embodiment of the present invention.
Fig. 3 is the block diagram of denitrification system according to an embodiment of the present invention.
Specific embodiment
With reference to the accompanying drawing, specific embodiments of the present invention will be described in detail, it is to be understood that guarantor of the invention Shield range is not limited by the specific implementation.
Unless otherwise explicitly stated, otherwise in entire disclosure and claims, term " includes " or its change Changing such as "comprising" or " including " etc. will be understood to comprise stated element or component, and not exclude other members Part or other component parts.
Fig. 1 is method flow diagram according to an embodiment of the present invention.As shown, biogas slurry nitrification denitrogenation reuse is controlled automatically Method processed includes:
Step 101: temperature, oxygen content and pH value in monitoring UASB reactor;
Step 102: if temperature, oxygen content in UASB reactor and one or more deviation first predetermined values in pH value Set is then adjusted one or more in temperature, oxygen content and the pH value in UASB reactor;
Step 103: the flow of biogas slurry and waste water of livestock poultry raw water in monitoring turbid water system, wherein biogas slurry is the production of UASB reactor Object;
Step 104: if the ratio between flow of biogas slurry and waste water of livestock poultry raw water deviates second predetermined value in turbid water system, to mixed water System is diagnosed, if it find that turbid water system water inlet blocks, then issues warning message, if not finding mixed water system System failure, then adjust the flow of biogas slurry Yu waste water of livestock poultry raw water;
Step 105: the dissolved oxygen in the micro- oxygen aeration tank of monitoring No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is dense Degree, pH value and ammonia nitrogen concentration;
Step 106: if the dissolved oxygen in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is dense One or more deviation second predetermined value set in degree, pH value and ammonia nitrogen concentration, then to the micro- oxygen aeration tank of No.1, No. two it is micro- One or more in oxygen aeration tank and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang are adjusted It is whole;
Step 107: the flow of the mixed liquor of monitoring No.1 micro- oxygen aeration tank institute received No. three aeration tanks Wei Yang generation;If mixed The flow for closing liquid deviates the 4th predetermined value, then diagnoses to No. three aeration tanks Wei Yang, if it find that No. three micro- oxygen are aerated water Road blocks, then issues the second warning message, if not finding No. three aeration tank Wei Yang failures, the flow of mixed liquor.
In other embodiments, if temperature, oxygen content in UASB reactor and in pH value it is one or more partially From first predetermined value set, then one or more in temperature, oxygen content and the pH value in UASB reactor are adjusted It specifically includes:
If temperature in UASB reactor is lower than UASB reactor predetermined temperature, control heating device to UASB reactor into Row heating;
If the oxygen content in UASB reactor is higher than UASB reactor oxygen content predetermined concentration, controls and open aspiration pump progress Pumping.
In other embodiments, if in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Dissolved oxygen concentration, one or more deviation second predetermined value set in pH value and ammonia nitrogen concentration, then the micro- oxygen of No.1 is exposed One in gas pond, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang Or multinomial be adjusted includes the following steps:
If any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is molten It solves oxygen concentration and is lower than micro- predetermined dissolved oxygen concentration in oxygen aeration tank, then control oxygen generator and be oxygenated to micro- oxygen aeration tank;
If the pH of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Value is lower than micro- predetermined pH value in oxygen aeration tank, then controls lye Chi Xiangwei oxygen aeration tank addition lye;
If the ammonia of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Nitrogen concentration is lower than micro- predetermined ammonia nitrogen concentration in oxygen aeration tank, then controls heating device and improve heating power.
In other embodiments, wherein micro- predetermined dissolved oxygen concentration in oxygen aeration tank for the micro- oxygen aeration tank of No.1 is 0.1-0.2mg/L, micro- predetermined dissolved oxygen concentration in oxygen aeration tank for No. two aeration tanks Wei Yang is 0.05-0.1mg/L, for three Micro- predetermined dissolved oxygen concentration in oxygen aeration tank of number aeration tank Wei Yang is 0-0.05mg/L.
In other embodiments, if it find that turbid water system water inlet blocks, then warning message is issued specifically: warp By cordless communication network, warning message is sent to wireless terminal;
Wherein, if it find that No. three aeration tanks Wei Yang water route blocks, then the second warning message is issued specifically: via wireless Communication network sends the second warning message to wireless terminal.
Fig. 2 is the block diagram of control system according to an embodiment of the present invention.As shown, control system of the invention 201 include:
UASB reactor monitors control module 202, is configured as:
Monitor temperature, oxygen content and the pH value in UASB reactor;
If temperature, oxygen content in UASB reactor and one or more deviation first predetermined value set in pH value, One or more in temperature, oxygen content and pH value in UASB reactor are adjusted;
Turbid water system monitors control module 203, is configured as:
Monitor the flow of biogas slurry and waste water of livestock poultry raw water in turbid water system, wherein biogas slurry is the product of UASB reactor;
If the ratio between flow of biogas slurry and waste water of livestock poultry raw water deviates second predetermined value in turbid water system, turbid water system is carried out Diagnosis, if it find that turbid water system water inlet blocks, then issues warning message, if not finding turbid water system failure, Then adjust the flow of biogas slurry Yu waste water of livestock poultry raw water;
Multiple micro- oxygen aeration tanks monitoring control modules (including first micro- oxygen aeration tank monitoring control module 204, second micro- oxygen aeration Pond monitors the micro- oxygen aeration tank of control module 205, third and monitors control module 206), it is configured as:
The micro- oxygen aeration tank of monitoring No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH in No. three aeration tanks Wei Yang respectively Value and ammonia nitrogen concentration;
If the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And one or more deviation second predetermined value set in ammonia nitrogen concentration, then to the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang And one or more in dissolved oxygen concentration, pH value and the ammonia nitrogen concentration in No. three aeration tanks Wei Yang are adjusted;
Monitor the flow of the mixed liquor of No.1 micro- oxygen aeration tank institute received No. three aeration tanks Wei Yang generation;If the stream of mixed liquor Amount deviates the 4th predetermined value, then diagnoses to No. three aeration tanks Wei Yang, if it find that No. three aeration tank Wei Yang water routes occur to block up Plug, then issue the second warning message, if not finding No. three aeration tank Wei Yang failures, the flow of mixed liquor.
In a preferred embodiment, if temperature, oxygen content in UASB reactor and one in pH value or Multinomial deviation first predetermined value set, then in temperature, oxygen content and the pH value in UASB reactor it is one or more into Row adjustment specifically includes:
If temperature in UASB reactor is lower than UASB reactor predetermined temperature, control heating device to UASB reactor into Row heating;
If the oxygen content in UASB reactor is higher than UASB reactor oxygen content predetermined concentration, controls and open aspiration pump progress Pumping.
In a preferred embodiment, if the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three micro- oxygen expose Dissolved oxygen concentration, pH value in gas pond and one or more deviation second predetermined value set in ammonia nitrogen concentration, then to No.1 In micro- oxygen aeration tank, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang One or more be adjusted include the following steps:
If any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is molten It solves oxygen concentration and is lower than micro- predetermined dissolved oxygen concentration in oxygen aeration tank, then control oxygen generator and be oxygenated to micro- oxygen aeration tank;
If the pH of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Value is lower than micro- predetermined pH value in oxygen aeration tank, then controls lye Chi Xiangwei oxygen aeration tank addition lye;
If the ammonia of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Nitrogen concentration is lower than micro- predetermined ammonia nitrogen concentration in oxygen aeration tank, then controls heating device and improve heating power.
In a preferred embodiment, wherein dense for micro- predetermined dissolved oxygen in oxygen aeration tank of the micro- oxygen aeration tank of No.1 Degree is 0.1-0.2mg/L, and micro- predetermined dissolved oxygen concentration in oxygen aeration tank for No. two aeration tanks Wei Yang is 0.05-0.1mg/L, needle Micro- predetermined dissolved oxygen concentration in oxygen aeration tank to No. three aeration tanks Wei Yang is 0-0.05mg/L.
In a preferred embodiment, if it find that turbid water system water inlet blocks, then warning message tool is issued Body are as follows: via cordless communication network, send warning message to wireless terminal;
Wherein, if it find that No. three aeration tanks Wei Yang water route blocks, then the second warning message is issued specifically: via wireless Communication network sends the second warning message to wireless terminal.
Fig. 3 is the block diagram of denitrification system according to an embodiment of the present invention.Denitrogenation processing system of the invention includes UASB reactor, turbid water system 301, Prepositive denitrification pond 302, first micro- oxygen aeration tank 303, second micro- oxygen aeration tank 304, Three micro- oxygen aeration tanks 305, sedimentation basin 306.Mixed liquor flows successively through turbid water system 301, Prepositive denitrification pond 302, first micro- oxygen Aeration tank 303, second micro- oxygen aeration tank 304, the micro- oxygen aeration tank 305 of third, sedimentation basin 306.Wherein, the micro- oxygen aeration tank of third Mixed liquor in 305 can be back to first micro- oxygen aeration tank 303.
The aforementioned description to specific exemplary embodiment of the invention is in order to illustrate and illustration purpose.These descriptions It is not wishing to limit the invention to disclosed precise forms, and it will be apparent that according to the above instruction, can much be changed And variation.The purpose of selecting and describing the exemplary embodiment is that explaining specific principle of the invention and its actually answering With so that those skilled in the art can be realized and utilize a variety of different exemplary implementation schemes of the invention and Various chooses and changes.The scope of the present invention is intended to be limited by claims and its equivalents.

Claims (10)

1. a kind of biogas slurry nitrifies denitrogenation reuse autocontrol method, it is characterised in that: the biogas slurry nitrification denitrogenation reuse is controlled automatically Method processed includes:
Monitor temperature, oxygen content and the pH value in UASB reactor;
If temperature, oxygen content in the UASB reactor and one or more deviation first predetermined value collection in pH value It closes, then one or more in temperature, oxygen content and the pH value in the UASB reactor is adjusted;
Monitor the flow of biogas slurry and waste water of livestock poultry raw water in turbid water system, wherein the biogas slurry is the production of the UASB reactor Object;
If the ratio between flow of biogas slurry and waste water of livestock poultry raw water deviates second predetermined value in turbid water system, turbid water system is carried out Diagnosis, if it find that turbid water system water inlet blocks, then issues warning message, if not finding turbid water system failure, Then adjust the flow of biogas slurry Yu waste water of livestock poultry raw water;
Monitor the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And ammonia nitrogen concentration;
If the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And one or more deviation second predetermined value set in ammonia nitrogen concentration, then to the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang And one or more in dissolved oxygen concentration, pH value and the ammonia nitrogen concentration in No. three aeration tanks Wei Yang are adjusted;
Monitor the flow of the mixed liquor of No.1 micro- oxygen aeration tank institute received No. three aeration tanks Wei Yang generation;If the stream of mixed liquor Amount deviates the 4th predetermined value, then diagnoses to No. three aeration tanks Wei Yang, if it find that No. three aeration tank Wei Yang water routes occur to block up Plug, then issue the second warning message, if not finding No. three aeration tank Wei Yang failures, the flow of mixed liquor.
2. biogas slurry as described in claim 1 nitrifies denitrogenation reuse autocontrol method, it is characterised in that: if the UASB is anti- One or more deviation first predetermined value set in temperature, oxygen content and the pH value in device are answered, then the UASB are reacted Temperature, oxygen content in device and one or more be adjusted in pH value specifically include:
If the temperature in the UASB reactor is lower than UASB reactor predetermined temperature, heating device is controlled to the UASB Reactor is heated;
If the oxygen content in the UASB reactor is higher than UASB reactor oxygen content predetermined concentration, opening aspiration pump is controlled It is evacuated.
3. biogas slurry as described in claim 1 nitrifies denitrogenation reuse autocontrol method, it is characterised in that: if the micro- oxygen of No.1 exposes One in gas pond, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang Or multinomial deviation second predetermined value set, then to the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang In dissolved oxygen concentration, one or more be adjusted in pH value and ammonia nitrogen concentration include the following steps:
If any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is molten It solves oxygen concentration and is lower than micro- predetermined dissolved oxygen concentration in oxygen aeration tank, then control oxygen generator and be oxygenated to micro- oxygen aeration tank;
If the pH of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Value is lower than micro- predetermined pH value in oxygen aeration tank, then controls lye pond to micro- oxygen aeration tank addition lye;
If the ammonia of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Nitrogen concentration is lower than micro- predetermined ammonia nitrogen concentration in oxygen aeration tank, then controls heating device and improve heating power.
4. biogas slurry as claimed in claim 3 nitrifies denitrogenation reuse autocontrol method, it is characterised in that: wherein, for described Micro- predetermined dissolved oxygen concentration in oxygen aeration tank of the micro- oxygen aeration tank of No.1 is 0.1-0.2mg/L, for No. two aeration tanks Wei Yang Micro- predetermined dissolved oxygen concentration in oxygen aeration tank be 0.05-0.1mg/L, it is pre- for micro- oxygen aeration tank of No. three aeration tanks Wei Yang Determining dissolved oxygen concentration is 0-0.05mg/L.
5. biogas slurry as described in claim 1 nitrifies denitrogenation reuse autocontrol method, it is characterised in that: if it find that mixed water system System water inlet blocks, then issues warning message specifically: via cordless communication network, sends the alarm to wireless terminal Message;
Wherein, if it find that No. three aeration tanks Wei Yang water route blocks, then the second warning message is issued specifically: via wireless Communication network sends second warning message to wireless terminal.
6. a kind of biogas slurry nitrifies denitrogenation reuse automatic control system, it is characterised in that: the biogas slurry nitrification denitrogenation reuse is controlled automatically System processed includes:
UASB reactor monitors control module, is configured as:
Monitor temperature, oxygen content and the pH value in UASB reactor;
If temperature, oxygen content in the UASB reactor and one or more deviation first predetermined value collection in pH value It closes, then one or more in temperature, oxygen content and the pH value in the UASB reactor is adjusted;
Turbid water system monitors control module, is configured as:
Monitor the flow of biogas slurry and waste water of livestock poultry raw water in turbid water system, wherein the biogas slurry is the production of the UASB reactor Object;
If the ratio between flow of biogas slurry and waste water of livestock poultry raw water deviates second predetermined value in turbid water system, turbid water system is carried out Diagnosis, if it find that turbid water system water inlet blocks, then issues warning message, if not finding turbid water system failure, Then adjust the flow of biogas slurry Yu waste water of livestock poultry raw water;
Multiple micro- oxygen aeration tanks monitor control module, are configured as:
Monitor the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And ammonia nitrogen concentration;
If the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and dissolved oxygen concentration in No. three aeration tanks Wei Yang, pH value with And one or more deviation second predetermined value set in ammonia nitrogen concentration, then to the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang And one or more in dissolved oxygen concentration, pH value and the ammonia nitrogen concentration in No. three aeration tanks Wei Yang are adjusted;
Monitor the flow of the mixed liquor of No.1 micro- oxygen aeration tank institute received No. three aeration tanks Wei Yang generation;If the stream of mixed liquor Amount deviates the 4th predetermined value, then diagnoses to No. three aeration tanks Wei Yang, if it find that No. three aeration tank Wei Yang water routes occur to block up Plug, then issue the second warning message, if not finding No. three aeration tank Wei Yang failures, the flow of mixed liquor.
7. biogas slurry as claimed in claim 6 nitrifies denitrogenation reuse automatic control system, it is characterised in that: if the UASB is anti- One or more deviation first predetermined value set in temperature, oxygen content and the pH value in device are answered, then the UASB are reacted Temperature, oxygen content in device and one or more be adjusted in pH value specifically include:
If the temperature in the UASB reactor is lower than UASB reactor predetermined temperature, heating device is controlled to the UASB Reactor is heated;
If the oxygen content in the UASB reactor is higher than UASB reactor oxygen content predetermined concentration, opening aspiration pump is controlled It is evacuated.
8. biogas slurry as claimed in claim 6 nitrifies denitrogenation reuse automatic control system, it is characterised in that: if the micro- oxygen of No.1 exposes One in gas pond, No. two aeration tanks Wei Yang and dissolved oxygen concentration, pH value and ammonia nitrogen concentration in No. three aeration tanks Wei Yang Or multinomial deviation second predetermined value set, then to the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang In dissolved oxygen concentration, one or more be adjusted in pH value and ammonia nitrogen concentration include the following steps:
If any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang is molten It solves oxygen concentration and is lower than micro- predetermined dissolved oxygen concentration in oxygen aeration tank, then control oxygen generator and be oxygenated to micro- oxygen aeration tank;
If the pH of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Value is lower than micro- predetermined pH value in oxygen aeration tank, then controls lye pond to micro- oxygen aeration tank addition lye;
If the ammonia of any micro- oxygen aeration tank in the micro- oxygen aeration tank of No.1, No. two aeration tanks Wei Yang and No. three aeration tanks Wei Yang Nitrogen concentration is lower than micro- predetermined ammonia nitrogen concentration in oxygen aeration tank, then controls heating device and improve heating power.
9. biogas slurry as claimed in claim 8 nitrifies denitrogenation reuse automatic control system, it is characterised in that: wherein, for described Micro- predetermined dissolved oxygen concentration in oxygen aeration tank of the micro- oxygen aeration tank of No.1 is 0.1-0.2mg/L, for No. two aeration tanks Wei Yang Micro- predetermined dissolved oxygen concentration in oxygen aeration tank be 0.05-0.1mg/L, it is pre- for micro- oxygen aeration tank of No. three aeration tanks Wei Yang Determining dissolved oxygen concentration is 0-0.05mg/L.
10. biogas slurry as claimed in claim 6 nitrifies denitrogenation reuse automatic control system, it is characterised in that: if it find that mixed water System water inlet blocks, then issues warning message specifically: via cordless communication network, sends the report to wireless terminal Alert message;
Wherein, if it find that No. three aeration tanks Wei Yang water route blocks, then the second warning message is issued specifically: via wireless Communication network sends second warning message to wireless terminal.
CN201810769357.4A 2018-07-13 2018-07-13 A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system Pending CN110422926A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810769357.4A CN110422926A (en) 2018-07-13 2018-07-13 A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810769357.4A CN110422926A (en) 2018-07-13 2018-07-13 A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system

Publications (1)

Publication Number Publication Date
CN110422926A true CN110422926A (en) 2019-11-08

Family

ID=68407197

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810769357.4A Pending CN110422926A (en) 2018-07-13 2018-07-13 A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system

Country Status (1)

Country Link
CN (1) CN110422926A (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3303352B2 (en) * 1992-09-17 2002-07-22 株式会社明電舎 Operation control method for batch activated sludge treatment
CN104407587A (en) * 2014-11-24 2015-03-11 黑龙江省能源环境研究院 Biogas fermentation process state control system and biogas fermentation process state control method thereof
CN205368029U (en) * 2015-12-22 2016-07-06 浙江大学 Breed low CN of waste water and remove carbon processing apparatus than high -efficient denitrogenation of anaerobism natural pond liquid
CN105776546A (en) * 2016-05-18 2016-07-20 扬州大学 Sewage shortcut nitrification system

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3303352B2 (en) * 1992-09-17 2002-07-22 株式会社明電舎 Operation control method for batch activated sludge treatment
CN104407587A (en) * 2014-11-24 2015-03-11 黑龙江省能源环境研究院 Biogas fermentation process state control system and biogas fermentation process state control method thereof
CN205368029U (en) * 2015-12-22 2016-07-06 浙江大学 Breed low CN of waste water and remove carbon processing apparatus than high -efficient denitrogenation of anaerobism natural pond liquid
CN105776546A (en) * 2016-05-18 2016-07-20 扬州大学 Sewage shortcut nitrification system

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
蔡伟娜等: ""温度对污泥厌氧发酵产酸过程的影响"", 《净水技术》 *

Similar Documents

Publication Publication Date Title
CN101759290B (en) Method for rapidly realizing and stably maintaining shortcut nitrification in continuous flow process
CN107827318B (en) Carbon and nitrogen removal device for middle and late landfill leachate and treatment method thereof
CN110078212B (en) Device for realizing anaerobic ammonia oxidation denitrification of continuous flow urban sewage and use method thereof
CN210122541U (en) Intelligent sewage advanced treatment system based on micro-nano bubble technology
CN103332788B (en) Multi-stage anaerobic-aerobic combined nitrogen and phosphorus removing device and method for rural domestic sewage
CN110589969B (en) High-efficiency stable synchronous denitrification and dephosphorization device and method for sewage treatment plant
CN210595439U (en) System for effect is carried in consumption reduction suitable for biological denitrogenation of oxidation ditch
CN111039383A (en) Carbon source adding method and system
CN111268796A (en) System and method for treating low C/N ratio domestic sewage by anaerobic/anoxic filler and staged water inlet three-stage AO
CN110655176B (en) Sewage treatment aeration rate feedforward control method based on clustering
CN113845224A (en) Process method suitable for treating sewage with low carbon-nitrogen ratio
CN110436614A (en) It is a kind of based on microalgae/activated sludge water treatment technology
CN216141333U (en) Carbon source adding optimization control system of AOA + MABR coupling process
CN113023889B (en) Carbon source adding optimization control system and method for AOA + MABR coupling process
CN107337325B (en) Integrated anaerobic ammonia oxidation device for treating urban sewage and operation method thereof
CN104556379A (en) Sewage biological denitrifying device and process
CN110422926A (en) A kind of biogas slurry nitrification denitrogenation reuse autocontrol method and system
CN204490676U (en) The diphasic anaerobic tubular membrane bio-reactor of process organic waste water
US20230002262A1 (en) Method for deep treatment of household waste leachate by biochemical process
CN207596677U (en) For middle and advanced stage landfill leachate carbon and nitrogen removal device
CN116589096A (en) Multi-mode AAO-MBR (anaerobic-anoxic-oxic-Membrane biological reactor) technical process control system and method
CN116119874A (en) Wastewater treatment system for realizing resource recovery and carbon emission and related method
CN115477388A (en) Ammonium nitrate wastewater treatment device and method
CN204939182U (en) A kind of Process for Treatment of Swine Wastewater system based on microbiological fuel cell
CN114538538A (en) Total nitrogen control system and method for sewage plant

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
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20191108