CN101810875A - Organic fertilizer aerobic fermentation odor treatment method - Google Patents

Organic fertilizer aerobic fermentation odor treatment method Download PDF

Info

Publication number
CN101810875A
CN101810875A CN200910009228A CN200910009228A CN101810875A CN 101810875 A CN101810875 A CN 101810875A CN 200910009228 A CN200910009228 A CN 200910009228A CN 200910009228 A CN200910009228 A CN 200910009228A CN 101810875 A CN101810875 A CN 101810875A
Authority
CN
China
Prior art keywords
odor
foul smell
organic fertilizer
gas
tunnel
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.)
Granted
Application number
CN200910009228A
Other languages
Chinese (zh)
Other versions
CN101810875B (en
Inventor
刘克锋
王红利
黄友诚
李爱和
李旭
张鹏辉
玉红
赵彰荣
石爱平
陈学珍
刘永光
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing University of Agriculture
Original Assignee
Beijing University of Agriculture
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Beijing University of Agriculture filed Critical Beijing University of Agriculture
Priority to CN 200910009228 priority Critical patent/CN101810875B/en
Publication of CN101810875A publication Critical patent/CN101810875A/en
Application granted granted Critical
Publication of CN101810875B publication Critical patent/CN101810875B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Fertilizers (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention relates to an organic fertilizer aerobic fermentation odor treatment method. The method comprises the following steps of: collecting odor generated in a production process of an organic fertilizer by using a gas-collecting device and then inputting the odor to a gas transportation channel provided with a swirl vane so as to change the moving direction and the flow speed of the odor; when the flow speed of the odor reaches more than 15m/s, allowing the gas to enter a vertical wind tunnel of which the bottom is provided with an accelerating impeller to increase the speed to be more than 25m/s; under the strong impact disturbance of an aerodynamic force, atomizing a removing agent, wherein the upper part of the vertical wind tunnel is provided with a removing agent spraying device; at the same time, forming a turbulent flow boundary layer on the wall of the wind tunnel; fully mixing the odor and the removing agent and performing a chemical and physical reaction of the odor and the removing agent; discharging the generated neutral solid granules and the reused solution to a sedimentation tank along the tunnel wall under the action of the gravity; and discharging the purified gas from an exhaust outlet at the top of the tunnel.

Description

Organic fertilizer aerobic fermentation odor treatment method
Technical field
The present invention relates to the technical field of air contaminant treatment in the environmental conservation.It is primarily aimed at is fertilizer factory when making good use of the aerobe fermentation mode and producing, to the processing method of the foul smell that produces in the sweat.
Background technology
Existing organic fertilizer production adopts the mode of aerobic fermentation to produce fertilizer mostly.In the aerobic fermentation process, can produce a large amount of foul smell that contains multiple compound compositions such as hydrogen sulfide, ammonia, sulfur dioxide.Adopt the deodorizing method of convection current washing and absorption at present mostly for the processing of these foul smell.
The method of convection current washing is to rely on foul smell relative with detergent mobile in washing facility from bottom to top from top to bottom, and reach the admixture of gas, liquid, the agent generation Chemical Physics that removes in admixture in the different components of foul smell and the detergent is reacted, produce neutral solid particle, stink substance is removed, and purified gas is discharged.
Adsorption method is that foul smell is drawn into the gas discharge channel that adsorbent is housed, and when gas passes through the passage of certain-length, adsorbent will have the material absorption of stink, and gas is purified to a certain extent.
Above-mentioned two kinds of methods all exist bigger limitation.
The defective of convection current washing method is: because foul smell is the bulk ascending motion, detergent liquid is the wire descending motion, in convection process up and down, just have undercompounding, reaction not exclusively removes the not high problem of stink substance efficient, and equipment volume is big, the operating cost height.
The defective of absorption method is: owing to be subjected to the restriction of adsorbents adsorb ability, reach adsorption effect preferably, just must strengthen the input amount of adsorbent and prolong sorption channel as far as possible, processing cost is huge.
Summary of the invention
The objective of the invention is to: provide a kind of odor removal efficient height, the odor treatment method that operating cost is low.Be mainly used in the processing of the foul smell that produces in the organic fertilizer aerobic fermentation process.
Technical scheme
Above-mentioned purpose of the present invention, can realize by following technological facilities:
The foul smell that produces in the organic fertilizer production process is collected with gas collecting apparatus, and foul smell is sucked gas distribution channel, establish swirl vane in the passage, be used to change the direction of motion of foul smell, improve the flowing velocity of foul smell by air-introduced machine.When the speed of foul smell reaches 15 meter per seconds when above, enter vertical wind tunnel, the wind-tunnel bottom is provided with speeding-up blade.Gas enters back speed and brings up to more than 25 meter per seconds, be provided with on wind-tunnel top and remove the agent flusher, under the powerful shock vibration of aerodynamic force, remove agent and be atomized, simultaneously form turbulent boundary layer at the hole of wind-tunnel wall, foul smell with remove the biochemical physical reactions of agent hybrid concurrency, neutral solid particle that produces and the solution that recycles, Dong Bi drains into sedimentation tank in the effect lower edge of gravity, purified gas, the air vent discharging through the top, hole.
Description of drawings
Fig. 1 is the odor removal sketch map among the present invention.
Shown in the figure: 1 gas pipeline 2 quickens impeller 3 vertical wind tunnels 4 flushers 5 air vents 6 observation windows
The specific embodiment
Below in conjunction with the running experiment of implementing and with reference to sketch map, provide the specific embodiment:
At first the foul smell of collecting is sucked in the gas distribution channel (1) by air-introduced machine, owing to be provided with swirl vane in the passage, gas rotation and quickening flow velocity under the effect of tangent line, when the mobile speed of foul smell reaches 15 meter per seconds when above, foul smell enters vertical wind tunnel (3), under the effect of quickening impeller (2), the flow velocity of foul smell continues to improve, and can reach more than 25 meter per seconds.On the top of wind-tunnel, be equipped with and remove agent flusher (4).Under the powerful shock vibration of aerodynamic force, removing agent is atomized, form turbulent boundary layer at the hole of wind-tunnel wall simultaneously, foul smell with remove the biochemical physical reactions of the abundant hybrid concurrency of agent, neutral solid particle that produces and the solution that recycles, Dong Bi drains into sedimentation tank in the effect lower edge of gravity, purified gas, air vent (5) discharging through the top, hole.
Experimental result detects proof, the method applied in the present invention, and the removal efficiency that can make stink substance is more than 95%, and use equipment is simple, operating cost is low, energy resource consumption is few, emission gases is up to standard.

Claims (3)

1. organic fertilizer aerobic fermentation odor treatment method, it is characterized in that: the foul smell of collecting is sucked in the gas distribution channel (1) by air-introduced machine, owing to be provided with swirl vane in the passage, gas rotation and accelerate flow velocity under the effect of tangent line is when the flow velocity of foul smell reaches 15 meter per seconds when above, foul smell enters vertical wind tunnel (3), under the effect of quickening impeller (2), the speed of foul smell continues to improve, and can reach more than 25 meter per seconds, on the top of wind-tunnel, be equipped with and remove agent flusher (4); Under the powerful shock vibration of aerodynamic force, removing agent is atomized, form turbulent boundary layer at the hole of wind-tunnel wall simultaneously, foul smell with remove the biochemical physical reactions of the abundant hybrid concurrency of agent, neutral solid particle that produces and the solution that recycles, Dong Bi drains into sedimentation tank in the effect lower edge of gravity, purified gas, air vent (5) discharging through the top, hole.
2. organic fertilizer aerobic fermentation odor treatment method as claimed in claim 1 is characterized in that: described acceleration impeller percent opening is 25-30%.
3. organic fertilizer aerobic fermentation odor treatment method as claimed in claim 1 is characterized in that: described to remove agent be calcium oxide solution.
CN 200910009228 2009-02-25 2009-02-25 Organic fertilizer aerobic fermentation odor treatment method Expired - Fee Related CN101810875B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN 200910009228 CN101810875B (en) 2009-02-25 2009-02-25 Organic fertilizer aerobic fermentation odor treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN 200910009228 CN101810875B (en) 2009-02-25 2009-02-25 Organic fertilizer aerobic fermentation odor treatment method

Publications (2)

Publication Number Publication Date
CN101810875A true CN101810875A (en) 2010-08-25
CN101810875B CN101810875B (en) 2013-03-20

Family

ID=42618334

Family Applications (1)

Application Number Title Priority Date Filing Date
CN 200910009228 Expired - Fee Related CN101810875B (en) 2009-02-25 2009-02-25 Organic fertilizer aerobic fermentation odor treatment method

Country Status (1)

Country Link
CN (1) CN101810875B (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1843827A1 (en) * 2005-02-03 2007-10-17 Jangshik Yun Centrifugal wet type air cleaner utilizing a spin vaporizer and a spiral on the basis of a labyrinth effect
CN201061627Y (en) * 2007-06-08 2008-05-21 连惠蓉 Improved construction of air fragrant purifier
CN201168548Y (en) * 2008-03-12 2008-12-24 北京农学院 Novel turbulence type waste gas treater

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1843827A1 (en) * 2005-02-03 2007-10-17 Jangshik Yun Centrifugal wet type air cleaner utilizing a spin vaporizer and a spiral on the basis of a labyrinth effect
CN201061627Y (en) * 2007-06-08 2008-05-21 连惠蓉 Improved construction of air fragrant purifier
CN201168548Y (en) * 2008-03-12 2008-12-24 北京农学院 Novel turbulence type waste gas treater

Also Published As

Publication number Publication date
CN101810875B (en) 2013-03-20

Similar Documents

Publication Publication Date Title
CN101259364A (en) Wet desulphurization technique for sintered flue gas
CN202725003U (en) Compound type multifunctional ammonia desulphurization device
CN102489132B (en) Novel dual-alkali desulfurization method for removal of sulfur dioxide from flue gas and generation of elemental sulfur as byproduct
CN203598644U (en) Flue gas desulfurization system
CN100591408C (en) Desulfurizing tower for wet fuel gas desulfurizing system
CN101066519A (en) Method of controlling fume speed inside desulfurizing absorption tower
CN101804296B (en) Deodorization device and method thereof
CN108654346B (en) Hydrochloric acid mist purification treatment device
CN105056732A (en) Waste gas treatment system
CN201735331U (en) Waste gas desulfurization device
CN204865533U (en) Gas treating system
CN203235395U (en) Flue gas desulfurization equipment
CN106474886A (en) A kind of industrial waste-gas purifier of low temperature plasma joint two-stage dynamic wave
CN101810875B (en) Organic fertilizer aerobic fermentation odor treatment method
CN201669049U (en) Deodorizing device
CN102247741B (en) Flue gas desulfurization process
CN105536409B (en) A kind of haze processing system
CN106861416A (en) SO in removing industrial waste gas2And NOXTechnique
CN200967755Y (en) Ammonia stripping absorption tower
CN205730844U (en) A kind of biochemical sewage exhaust-gas efficient deodorization processing means
CN102500209A (en) Comprehensive smoke purifying tower based on nanometer activated carbon adsorption and ozone technology
CN203635064U (en) Flue gas desulfurization and wet dust removal combined purification device
CN207445965U (en) A kind of lime stone-gypsum wet flue gas desulfurizing demister
CN204656166U (en) A kind of have the Cyclonic gas-liquid separation device collecting microlayer model
CN107952312A (en) A kind of desulfurization dust-removing technique of flue gas cleaning discharge

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20130320

Termination date: 20140225