CN108392977A - A kind of bio-trickling integration apparatus and its application - Google Patents
A kind of bio-trickling integration apparatus and its application Download PDFInfo
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- CN108392977A CN108392977A CN201810536591.2A CN201810536591A CN108392977A CN 108392977 A CN108392977 A CN 108392977A CN 201810536591 A CN201810536591 A CN 201810536591A CN 108392977 A CN108392977 A CN 108392977A
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- baffle
- trickling
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- integration apparatus
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- 230000010354 integration Effects 0.000 title claims abstract description 32
- 239000007789 gas Substances 0.000 claims abstract description 71
- 239000012855 volatile organic compound Substances 0.000 claims abstract description 47
- 238000007781 pre-processing Methods 0.000 claims abstract description 27
- 239000007921 spray Substances 0.000 claims description 36
- 239000000945 filler Substances 0.000 claims description 20
- 239000012530 fluid Substances 0.000 claims description 16
- 229920002635 polyurethane Polymers 0.000 claims description 6
- 239000004814 polyurethane Substances 0.000 claims description 6
- 239000000463 material Substances 0.000 claims description 4
- 230000015556 catabolic process Effects 0.000 abstract description 5
- 238000006731 degradation reaction Methods 0.000 abstract description 5
- 239000005416 organic matter Substances 0.000 abstract description 4
- 239000007788 liquid Substances 0.000 description 17
- 238000000034 method Methods 0.000 description 11
- 244000005700 microbiome Species 0.000 description 8
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 6
- 235000015097 nutrients Nutrition 0.000 description 6
- 238000010521 absorption reaction Methods 0.000 description 5
- 239000000428 dust Substances 0.000 description 5
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 4
- LSDPWZHWYPCBBB-UHFFFAOYSA-N Methanethiol Chemical compound SC LSDPWZHWYPCBBB-UHFFFAOYSA-N 0.000 description 4
- 229910021529 ammonia Inorganic materials 0.000 description 4
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 238000005192 partition Methods 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 3
- 229910001220 stainless steel Inorganic materials 0.000 description 3
- 239000010935 stainless steel Substances 0.000 description 3
- RTZKZFJDLAIYFH-UHFFFAOYSA-N Diethyl ether Chemical compound CCOCC RTZKZFJDLAIYFH-UHFFFAOYSA-N 0.000 description 2
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 2
- 238000011953 bioanalysis Methods 0.000 description 2
- 238000004173 biogeochemical cycle Methods 0.000 description 2
- 238000009395 breeding Methods 0.000 description 2
- 230000001488 breeding effect Effects 0.000 description 2
- 238000009841 combustion method Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000006303 photolysis reaction Methods 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 230000003134 recirculating effect Effects 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 239000002904 solvent Substances 0.000 description 2
- 239000002912 waste gas Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- 239000007836 KH2PO4 Substances 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 150000001299 aldehydes Chemical class 0.000 description 1
- 150000001335 aliphatic alkanes Chemical class 0.000 description 1
- 150000001336 alkenes Chemical class 0.000 description 1
- 150000001345 alkine derivatives Chemical class 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 150000004945 aromatic hydrocarbons Chemical class 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical group [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000002306 biochemical method Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002576 ketones Chemical class 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Natural products C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 1
- -1 methane hydrocarbon Chemical class 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 238000006552 photochemical reaction Methods 0.000 description 1
- GNSKLFRGEWLPPA-UHFFFAOYSA-M potassium dihydrogen phosphate Chemical compound [K+].OP(O)([O-])=O GNSKLFRGEWLPPA-UHFFFAOYSA-M 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 150000003384 small molecules Chemical class 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/84—Biological processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/38—Removing components of undefined structure
- B01D53/44—Organic components
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/485—Sulfur compounds containing only one sulfur compound other than sulfur oxides or hydrogen sulfide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/52—Hydrogen sulfide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/54—Nitrogen compounds
- B01D53/58—Ammonia
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/70—Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
- B01D2257/708—Volatile organic compounds V.O.C.'s
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Molecular Biology (AREA)
- Treating Waste Gases (AREA)
Abstract
The present invention provides a kind of bio-trickling integration apparatus and its applications, belong to volatile organic matter (VOCs) degradation equipment technical field, the bio-trickling integration apparatus includes the preprocessing module being sequentially arranged in main box, first baffle (5), second baffle (6) and bio-trickling module;The preprocessing module is separated with bio-trickling module by first baffle (5) and second baffle (6);The first baffle (5) is fixedly connected with main box bottom;It is fixedly connected at the top of the second baffle (6) and main box;Gap between gap, the first baffle (5) between at the top of the first baffle (5) and main box and the gap between second baffle (6), the second baffle (6) and main box bottom forms gas passage.The bio-trickling integration apparatus realizes pretreatment and the bio-trickling of VOCs gases in same main box, reduces the floor space of entire processing unit.
Description
Technical field
The invention belongs to volatile organic matter (VOCs) degradation equipment technical field more particularly to a kind of bio-trickling one
Change equipment and its application.
Background technology
Volatile organic matter (VOCs) refers to participating in the organic compound of atmospheric photochemical reaction, including non-methane hydrocarbon
(alkane, alkene, alkynes, aromatic hydrocarbon etc.), chlorinated organics, itrogenous organic substance, contains oxygen-bearing organic matter (aldehyde, ketone, alcohol, ether etc.)
Sulfur organic etc. is to form ozone (O3) and fine particle (PM2.5) pollution important as precursors object.The sources VOCs are wide, harm is big,
Difficult, China extremely payes attention to the improvement of VOCs, and VOCs control technologies are broadly divided into solvent absorption, absorption at present
Method, condensing recovery, low-temperature plasma, UV photodissociation, combustion method and bioanalysis, condensing recovery method is due to being only limitted to the useless of single component
Gas, application range are limited;Solvent absorption, low-temperature plasma, UV photodissociation treatment effeciencies are extremely low, are also easy to produce ozone or small molecule etc.
Pollutant, therefore, it is difficult to promote and apply.
Compared with Traditional materialized method (such as absorption method, combustion method), bioanalysis has easy to operate, economical and efficient, nothing
The features such as secondary pollution, becomes the emerging focus of VOCs improvement.It is common for biology drop in the equipment of Biochemical method VOCs
Equipment is filtered, in the engineering process that VOCs is handled due to biological island, exhaust gas need to be adjusted to the condition of suitable micro-organisms growth, example
Such as:PH value is 6~8, temperature is 25~35 DEG C, and exhaust gas temperature and pH are not necessarily met the requirements in project treatment, is given up simultaneously
Dust can also be carried in gas secretly, therefore must be pre-processed before exhaust gas enters biological case, the pretreated purpose is removal
PH and temperature are adjusted to the condition of suitable micro-organisms growth by dust, particle in exhaust gas.The pre- place of VOCs exhaust gas in the prior art
Reason generally using the wet treatment method of spray, carries out in special pre-processing device, then will be pre-processed with gas piping
Equipment is connect with bio-trickling case, and VOCs engineering exhaust gas, into bio-trickling case, is dropped after pre-processing device by microorganism
Solution.But current this method takes up a large area, the equipment that uses is more and special VOCs exhaust pipes is needed to connect,
Processing procedure is easy pollution.
Invention content
In view of this, the purpose of the present invention is to provide a kind of VOCs pretreatments and life simple in structure, floor space is small
Object drop filter integration apparatus and its application.
In order to achieve the above-mentioned object of the invention, the present invention provides following technical scheme:A kind of bio-trickling integration apparatus, packet
Include the preprocessing module being sequentially arranged in main box, first baffle (5), second baffle (6) and bio-trickling module;The pre- place
Reason module is separated with bio-trickling module by first baffle (5) and second baffle (6);The first baffle (5) and main box
Bottom is fixedly connected;It is fixedly connected at the top of the second baffle (6) and main box;The first baffle (5) and main box top
Between gap, the gap between the first baffle (5) and second baffle (6), the second baffle (6) and main box bottom
Between gap formed gas passage.With 4000m3The exhaust-gas treatment gauge of/h
Preferably, the height of the first baffle (5) and second baffle (6) be independently main box height 60~
90%.
Preferably, the level interval of the first baffle (5) and second baffle (6) is 0.2~0.3m.
Preferably, the floor space of told main box is 10~17m2。
Preferably, the preprocessing module includes the first leakage fluid dram (1), air inlet (2) and the first spray port (4).
Preferably, the bio-trickling module includes the second leakage fluid dram (11), filler (9), the second spray port (8) and outlet
Mouth (7).
Preferably, first spray port (4) and the second spray port (8) are independent including several nozzles.
Preferably, the filler (9) is polyurethane filler.
The present invention also provides application of the bio-trickling integration apparatus in handling VOCs gases.
Beneficial effects of the present invention:Bio-trickling integration apparatus provided by the invention passes through in same main box
One baffle (5) and second baffle (6) separate the preprocessing module and bio-trickling module, and VOCs gases are from main box bottom
Air inlet (2) enter, after preprocessing module removes dust particles, adjusts pH value and temperature, by first baffle (5),
It degrades into bio-trickling module behind the gas passage that main box is formed with second baffle (6), it is real in same main box
Pretreatment and the bio-trickling for having showed VOCs gases, simplify entire processing unit, reduce the occupation of land face of entire processing unit
Product, that shortens VOCs gases passes through the time.
Description of the drawings
Fig. 1 is the bio-trickling integration apparatus in the embodiment of the present invention 1;
Fig. 2 is bio-trickling equipment structure chart in the prior art.
Specific implementation mode
The present invention provides a kind of bio-trickling integration apparatus, and structure is as shown in Fig. 1, including is sequentially set in main box
Preprocessing module, first baffle (5), second baffle (6) and the bio-trickling module set;The preprocessing module and bio-trickling
Module is separated by first baffle (5) and second baffle (6);The first baffle (5) is fixedly connected with main box bottom;It is described
It is fixedly connected at the top of second baffle (6) and main box;Gap between at the top of the first baffle (5) and main box, described the
Gap, the second baffle (6) between one baffle (5) and second baffle (6) and the gap between main box bottom form gas
Body access.
In the present invention, the bio-trickling integration apparatus includes a main box, the preprocessing module and biology
Drop filter module is respectively positioned on inside main box.In the present invention, the material of the main box is preferably stainless steel;The main box
Floor space be preferably 15m2;The bio-trickling integration apparatus is preferably 3000 for the treating capacity of VOCs gases~
5000m3/ h, more preferably 4000m3/h。
In the present invention, the bio-trickling integration apparatus includes preprocessing module, and the preprocessing module is preferred
It include the air inlet (2) positioned at main box one side;The air inlet (2) is apart from main box bottom 0.5m;The air inlet (2)
Size be preferably 0.1~0.2m2, more preferably 0.15m2;The effect of the air inlet (2) is to make institute in the present invention
VOCs gases are stated to enter in main box.
In the present invention, the preprocessing module further includes the first spray port (4) hung at the top of main box, in this hair
First spray port (4) described in bright preferably include 2~4 nozzles, more preferably 3.The work of first spray port (4)
With to adjust liquid to VOCs gas showers pH, to adjust the pH value of VOCs gases, while the dust carried secretly in VOCs gases is removed
Particle.The pH adjusts liquid and is preferably hydrochloric acid in the present invention.
In the present invention, the preprocessing module further includes the first leakage fluid dram (1), in the present invention first leakage fluid dram
(1) it is located at 0.3~0.4m under main box one side air inlet (2);More preferably 0.4m.In the present invention, the first row
The pH that first spray port (4) sprays that act as being discharged of liquid mouth (1) adjusts liquid, to ensure to pre-process liquid level (3) in template
Less than air inlet (2).
In the present invention, first baffle (5), in the present invention, the first baffle are provided with after the preprocessing module
(5) highly preferred is 60~90%, more preferably the 70~80% of main box height.In the present invention, the first gear
Plate (5) is fixedly connected with main box bottom, and described be fixedly connected preferably is welded;The material of the first baffle (5) is preferred
It is stainless steel, in the present invention, the first baffle (5) act as separating preprocessing module and bio-trickling module, together
When for pretreated VOCs gases flow out gap, VOCs gases are entered by the gas passage in bio-trickling module.
In the present invention, second baffle (6), in the present invention, the second baffle is arranged in the first baffle (5) afterwards
(6) highly preferred is 60~90%, more preferably the 70~80% of main box height;The second baffle (6) and main tank
It is fixedly connected at the top of body, described be fixedly connected preferably is welded;The material of the second baffle (6) is preferably stainless
Steel.In the present invention, the second baffle (6) and the level interval of first baffle (5) are preferably 0.2-0.3m, more preferably
0.25m.In the present invention, the second baffle (6) act as separating preprocessing module and bio-trickling module, while being pre-
Treated, and VOCs gases flow out gap, and VOCs gases are entered by the gas passage in bio-trickling module.
Further include bio-trickling module in the bio-trickling integration apparatus in the present invention.The bio-trickling module
Including the second leakage fluid dram (11), filler (9), the second spray port (8) and gas outlet (7).In the present invention, second spray port
(8) include preferably several nozzles, preferably 6~10, more preferably 7~9.In the present invention, described second
Spray port (8) is act as to filler (9) spray Nutrient Cycle liquid, and promotion is adsorbed on the rapid microbial growth on filler (9)
Breeding, improves the degradation efficiency of VOCs.In the present invention, the Nutrient Cycle liquid includes preferably KH2PO4(NH4)2SO4;Institute
The spray rate for stating recirculating nutrient solution is 280~320ml/min.
In the present invention, second leakage fluid dram (11) is preferably located at main box and the opposite side of the first leakage fluid dram (1)
Face bottom, in the present invention second leakage fluid dram (11) act as by the recirculating nutrient solution body be discharged, it is ensured that main box
The liquid level (10) of interior bio-trickling module is less than filler (9).In the present invention, the filler (9) is preferably polyurethane filler.
In the present invention, the polyurethane filler can effectively adsorb VOCs degrading microorganisms.
In the present invention, the bio-trickling module further includes gas outlet (7), in the present invention, gas outlet (7) position
At the top of the main box, the gas outlet (7) act as degrade after uncontaminated gases be discharged.
The present invention also provides application of the bio-trickling integration apparatus in handling VOCs.In the present invention, institute
It states to apply and specifically includes following procedure:Pending VOCs gases enter main box by the air inlet (2) of main box one side
It is interior, from bottom to top by preprocessing module, during the VOCs gases are by preprocessing module, the first spray port (4) to
It is 6~8 that the VOCs gas showers pH, which adjusts liquid and adjusts the pH value of VOCs gases, and settles the dust of the VOCs gases entrainment
Particle.The gas formed between first baffle (5) and second baffle (6) is passed through by pretreated VOCs gases
Access reaches bio-trickling module.In the present invention, the pretreated VOCs gases bio-trickling module from bottom to top
By filler (9), the VOCs gases are degraded to free of contamination gas by the microorganism adsorbed on filler (9);It is described pollution-free
Gas through gas outlet (7) be discharged.In the present invention, the VOCs gases are by bio-trickling module process, second sprays
The growth and breeding of mouth (8) microorganism of Sprayer Circulation nutrient solution maintenance downwards.
A kind of bio-trickling integration apparatus provided by the invention and its application are carried out with reference to embodiment detailed
Illustrate, but they cannot be interpreted as limiting the scope of the present invention.
Embodiment 1
Bio-trickling integration apparatus, concrete structure is as shown in Figure 1, wherein 1 is the first leakage fluid dram, and 2 be air inlet, and 3 are
The liquid level of preprocessing module, 4 be the first spray port, and 5 be first partition, and 6 be second partition, and 7 be gas outlet, and 8 be the second spray
Mouthful, 9 be filler, and 10 be the liquid level 11 of bio-trickling module be the second leakage fluid dram.
Bio-trickling integration apparatus, main box height 2.6m, total floor space 12.1m2, air inlet port size is diameter
The height of 450mm, first baffle are 2m2, the height of second baffle is 2m, and filler is fixed on bio-trickling module by baton round
Interior, 8 nozzles are arranged in packed height 1.2m, the first spray port, and spray pH adjusts liquid, and 62 nozzles are arranged in the second spray port,
Sprayer Circulation nutrient solution.For air quantity 4000m3/ h, 300~500mg/m of concentration3Ammonia, hydrogen sulfide waste gas treatment effeciency be
86%.
Embodiment 2
Bio-trickling integration apparatus, concrete structure is as shown in Figure 1, wherein 1 is the first leakage fluid dram, and 2 be air inlet, and 3 are
The liquid level of preprocessing module, 4 be the first spray port, and 5 be first partition, and 6 be second partition, and 7 be gas outlet, and 8 be the second spray
Mouthful, 9 be filler, and 10 be the liquid level 11 of bio-trickling module be the second leakage fluid dram.
Bio-trickling integration apparatus, main box height 2.4m, total floor space 15.0m2, air inlet port size is diameter
The height of 450mm, first baffle are 2m2, the height of second baffle is 2m, and filler is fixed on bio-trickling module by baton round
Interior, 8 nozzles are arranged in packed height 1.2m, the first spray port, and spray pH adjusts liquid, and 62 nozzles are arranged in the second spray port,
Sprayer Circulation nutrient solution.For air quantity 4000m3/ h, 300~500mg/m of concentration3Ammonia, hydrogen sulfide waste gas treatment effeciency be
93%.
Embodiment 3
VOCs gases are handled using the bio-trickling integration apparatus described in embodiment 1
VOCs gases composition includes ammonia, hydrogen sulfide, methyl mercaptan, the source Shandong sewage treatment plant of VOCs gases, into
Tolerance is 4000m3/ h, a concentration of 200~600mg/m3Exhaust gas is entered from air inlet in main box by air pump, is led to from bottom to top
Preprocessing module is crossed, the first spray port sprays hydrochloric acid, spray rate 3m3/ h, the pH value of pretreated exhaust gas is 6.5~
7.5, the waste liquid of preprocessing module is discharged by the first leakage fluid dram;Pretreated exhaust gas passes through second baffle and second
The gas passage of baffle composition enters bio-trickling module, exhaust gas in bio-trickling module from bottom to top by polyurethane filler,
The microorganism species of absorption degradation VOCs gases on polyurethane filler, exhaust gas is after the degradation of microorganism species, by gas outlet
Discharge, in exhaust gas is by bio-trickling module process, the downward Sprayer Circulation nutrient solution of the second spray port, spray rate
0.45m3The waste liquid of/h, bio-trickling module are discharged by the second leakage fluid dram.
The floor space of whole equipment is 15m2, the residence time of exhaust-gas treatment is 15s, treatment effeciency 91%.
Comparative example 1
The separated abatement equipment of existing conventional pretreatment and bio-trickling is 4000m for processing air quantity3/ h's is useless
Gas, pollutant are ammonia, hydrogen sulfide, methyl mercaptan, 200~600mg/m of concentration3, floor space 20m2, treatment effeciency 92%.
By above-described embodiment it is found that bio-trickling integration apparatus provided by the invention realizes in same main box
The pretreatment of VOCs gases and bio-trickling simplify entire processing unit, reduce the floor space of entire processing unit, contracting
Short VOCs gases by the time, improve the treatment effeciency of VOCs gases.
The above is only a preferred embodiment of the present invention, it is noted that for the ordinary skill people of the art
For member, various improvements and modifications may be made without departing from the principle of the present invention, these improvements and modifications are also answered
It is considered as protection scope of the present invention.
Claims (9)
1. a kind of bio-trickling integration apparatus, which is characterized in that including be sequentially arranged in main box preprocessing module, first
Baffle (5), second baffle (6) and bio-trickling module;The preprocessing module passes through first baffle (5) with bio-trickling module
It is separated with second baffle (6);The first baffle (5) is fixedly connected with main box bottom;The second baffle (6) and main box
Top is fixedly connected;Gap, the first baffle (5) and second baffle between at the top of the first baffle (5) and main box
(6) gap, the second baffle (6) between and the gap between main box bottom form gas passage.
2. bio-trickling integration apparatus according to claim 1, which is characterized in that the first baffle (5) and second
The height of baffle (6) is independently the 60~90% of main box height.
3. bio-trickling integration apparatus according to claim 1, which is characterized in that the first baffle (5) and second
The level interval of baffle (6) is 0.2~0.3m.
4. the bio-trickling integration apparatus according to claims 1 to 3 any one, which is characterized in that with 4000m3/ h's
The floor space of exhaust-gas treatment gauge, the main box is 10~17m2。
5. bio-trickling integration apparatus according to claim 1, which is characterized in that the preprocessing module includes first
Leakage fluid dram (1), air inlet (2) and the first spray port (4).
6. bio-trickling integration apparatus according to claim 1, which is characterized in that the bio-trickling module includes the
Two leakage fluid drams (11), filler (9), the second spray port (8) and gas outlet (7).
7. bio-trickling integration apparatus according to claim 5 or 6, which is characterized in that first spray port (4) or
Independent second spray port (8) includes several nozzles.
8. bio-trickling integration apparatus according to claim 1, which is characterized in that the filler (9) is filled out for polyurethane
Material.
9. application of the bio-trickling integration apparatus in handling VOCs gases described in claim 1~8 any one.
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CN205760607U (en) * | 2016-05-16 | 2016-12-07 | 东莞市环境科学研究所 | A kind of compound bio bed cleaning equipment of VOCs |
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Inventor after: Yao Li Inventor after: Shi Yantao Inventor after: Zhu Yuxuan Inventor before: Yao Li Inventor before: Shi Yantao Inventor before: Zhu Yuxuan Inventor before: Han Yifan |
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Application publication date: 20180814 |