CN221514003U - Deodorization system and garbage station - Google Patents
Deodorization system and garbage station Download PDFInfo
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- CN221514003U CN221514003U CN202323102284.9U CN202323102284U CN221514003U CN 221514003 U CN221514003 U CN 221514003U CN 202323102284 U CN202323102284 U CN 202323102284U CN 221514003 U CN221514003 U CN 221514003U
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- 238000004332 deodorization Methods 0.000 title abstract description 7
- 239000012855 volatile organic compound Substances 0.000 claims abstract description 73
- 239000002808 molecular sieve Substances 0.000 claims abstract description 53
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims abstract description 53
- 238000003795 desorption Methods 0.000 claims abstract description 49
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 45
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 45
- 239000010457 zeolite Substances 0.000 claims abstract description 45
- 230000001877 deodorizing effect Effects 0.000 claims abstract description 37
- 230000003009 desulfurizing effect Effects 0.000 claims abstract description 29
- 239000000428 dust Substances 0.000 claims abstract description 28
- 239000002699 waste material Substances 0.000 claims abstract description 25
- 238000001179 sorption measurement Methods 0.000 claims abstract description 21
- 238000000746 purification Methods 0.000 claims abstract description 12
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims abstract description 10
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims abstract description 10
- 238000007599 discharging Methods 0.000 claims abstract description 7
- 239000007789 gas Substances 0.000 claims description 31
- 238000010438 heat treatment Methods 0.000 claims description 18
- 238000011144 upstream manufacturing Methods 0.000 claims description 18
- 239000003795 chemical substances by application Substances 0.000 claims description 13
- 239000007787 solid Substances 0.000 claims description 11
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 claims description 10
- 238000001914 filtration Methods 0.000 claims description 6
- 230000003647 oxidation Effects 0.000 claims description 4
- 238000007254 oxidation reaction Methods 0.000 claims description 4
- 238000010926 purge Methods 0.000 claims description 4
- 230000001172 regenerating effect Effects 0.000 claims description 4
- 238000004891 communication Methods 0.000 claims description 3
- 238000005485 electric heating Methods 0.000 claims description 2
- 238000012856 packing Methods 0.000 claims 2
- 238000000034 method Methods 0.000 abstract description 15
- 230000008929 regeneration Effects 0.000 abstract description 6
- 238000011069 regeneration method Methods 0.000 abstract description 6
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 7
- 238000005406 washing Methods 0.000 description 7
- 239000012071 phase Substances 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 238000006477 desulfuration reaction Methods 0.000 description 4
- 230000023556 desulfurization Effects 0.000 description 4
- 238000011049 filling Methods 0.000 description 4
- 239000007791 liquid phase Substances 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 229910021529 ammonia Inorganic materials 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000002918 waste heat Substances 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- 238000010521 absorption reaction Methods 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 239000002920 hazardous waste Substances 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- MBMLMWLHJBBADN-UHFFFAOYSA-N Ferrous sulfide Chemical compound [Fe]=S MBMLMWLHJBBADN-UHFFFAOYSA-N 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000001788 irregular Effects 0.000 description 1
- 238000006303 photolysis reaction Methods 0.000 description 1
- 230000015843 photosynthesis, light reaction Effects 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
Classifications
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- 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
- Treating Waste Gases (AREA)
Abstract
The utility model belongs to the field of deodorization, and discloses a deodorizing system and a garbage station, wherein the deodorizing system is used for treating odor in a mode of a dust removing device, a desulfurizing device and a VOCs treatment assembly containing zeolite molecular sieves, which are matched with a purifying pipeline and a waste discharging pipeline, wherein the dust removing device and the desulfurizing device can be used for removing dust and hydrogen sulfide in the odor respectively, the zeolite molecular sieves in the VOCs treatment assembly can be used for efficiently removing water-soluble and water-insoluble components in the odor, and especially, the treatment efficiency of the water-insoluble components is greatly improved compared with that of the traditional deodorizing process, so that the odor emission concentration can be greatly reduced. In addition, the adsorption, desorption and regeneration of the zeolite molecular sieve can be realized by matching with other parts in the VOCs treatment assembly such as the heat exchange unit, the purification pipeline and the waste discharge pipeline, so that the deodorizing system can be ensured to stably deodorize for a long time.
Description
Technical Field
The utility model relates to the technical field of deodorization, in particular to a deodorizing system and a garbage station.
Background
The garbage station can generate malodorous substances in the garbage unloading, compressing and transferring processes, and the main deodorizing process in the current industry is as follows: the dust-removed odor is firstly subjected to acid washing to remove water-soluble alkaline gases such as ammonia gas and the like, and then subjected to alkali washing to remove water-soluble acidic gases such as hydrogen sulfide and the like, and because the washing efficiency of the washing tower is limited, a large amount of water-soluble VOCs (volatile organic compounds, namely volatile organic compounds) exist in the odor subjected to two-stage washing, so that the odor is generally further sent into a biological filter and stays for a long time, and the content of the water-soluble VOCs in the odor is effectively reduced.
However, the acid washing, alkali washing and biological filter in the main stream deodorization process have insufficient treatment capacity on water-insoluble odor components, and the odor emission concentration is still difficult to be reduced to a lower level in practice; in the case of the conventional plasma catalysis and UV photolysis processes, although the process has the capability of treating water-insoluble odor components, the process has low treatment efficiency and is not suitable for being used as a deodorizing main process.
Disclosure of utility model
Aiming at the defects or shortcomings in the prior art, the utility model provides a deodorizing system and a garbage station, which can efficiently remove water-soluble and water-insoluble components in odor so as to solve the problem of short plates with insufficient treatment efficiency of the main flow deodorizing technology on the water-insoluble components, and realize the aim of greatly reducing the odor emission concentration.
To achieve the above object, a first aspect of the present utility model provides a deodorizing system comprising:
The dust removing device and the desulfurizing device are respectively used for removing dust and hydrogen sulfide of odor;
The VOCs treatment assembly comprises a VOCs treatment unit, an adsorption fan, a desorption fan, a heating device, a tail end treatment device and a heat exchange unit, wherein the VOCs treatment unit comprises a zeolite molecular sieve capable of removing VOCs in odor, and the heat exchange unit can cool the zeolite molecular sieve after desorption and heating;
the purification pipeline is connected with the dust removing device, the desulfurizing device and the VOCs treatment unit in series along the direction from the upstream end to the downstream end, the purification pipeline is also connected with the adsorption fan in series, the upstream end of the purification pipeline is an odor input end, and the downstream end of the purification pipeline is a purified gas output end;
The waste discharge pipeline is connected in series with the heating device, the VOCs treatment unit and the tail end treatment device along the direction from the upstream end to the downstream end, the waste discharge pipeline is also connected in series with the desorption fan, and the upstream end of the waste discharge pipeline is a desorption gas input end and the downstream end is a desorption gas output end.
Optionally, the VOCs treatment unit further comprises an upstream flow distribution chamber, a molecular sieve filling chamber and a downstream flow distribution chamber which are sequentially in airflow communication, and the molecular sieve filling chamber is filled with the zeolite molecular sieve.
Optionally, a plurality of VOCs processing units are arranged in the VOCs processing assembly, and the VOCs processing units are arranged in parallel in the purifying pipeline and the waste discharging pipeline.
Optionally, the heat exchange unit comprises a heat exchange medium, a first heat exchange structure, a compressor, a second heat exchange structure and an expansion valve, wherein the first heat exchange structure, the compressor, the second heat exchange structure and the expansion valve are connected in a closed loop through a pipeline so as to enable the heat exchange medium to circularly flow;
The first heat exchange structure is in heat exchange contact with the zeolite molecular sieve and can cool the zeolite molecular sieve after desorption and temperature rise, and the second heat exchange structure is formed into a preheating device which is connected in series in the waste discharge pipeline and is positioned at the upstream of the heating device.
Optionally, the first heat exchange structure includes a pre-buried heat exchange tube, and the pre-buried heat exchange tube is at least partially pre-buried in the zeolite molecular sieve.
Optionally, the desulfurizing device is filled with a solid desulfurizing agent; and/or the dust removing device is internally provided with a multi-layer filtering structure.
Optionally, the solid desulfurizing agent comprises an iron oxide desulfurizing agent, and the multi-layer filtering structure comprises a primary filter screen and a secondary filter bag which are arranged in a layered manner.
Optionally, the heating device is an electric heater; and/or the end treatment device is a regenerative oxidation furnace taking electric heating as a heat source.
Optionally, the adsorption blower is disposed between the VOCs treatment unit and the purge gas output end; and/or the desorption fan is arranged between the VOCs treatment unit and the tail end treatment device.
The second aspect of the utility model also provides a waste station comprising the deodorizing system.
Through the technical scheme, the deodorizing system disclosed by the utility model treats the odor in the form of the dust removing device, the desulfurizing device and the VOCs treatment assembly containing the zeolite molecular sieve, which are matched with the purifying pipeline and the waste discharging pipeline, wherein the dust removing device and the desulfurizing device can remove dust and hydrogen sulfide in the odor respectively, the zeolite molecular sieve in the VOCs treatment assembly can remove water-soluble and water-insoluble components in the odor efficiently, and especially the treatment efficiency of the water-insoluble components is greatly improved compared with that of the conventional deodorizing process, so that the odor emission concentration can be greatly reduced. In addition, the adsorption, desorption and regeneration of the zeolite molecular sieve can be realized by matching with other parts in the VOCs treatment assembly such as the heat exchange unit, the purification pipeline and the waste discharge pipeline, so that the deodorizing system can be ensured to stably deodorize for a long time.
Additional features and advantages of the utility model will be set forth in the detailed description which follows.
Drawings
The accompanying drawings are included to provide a further understanding of the utility model, and are incorporated in and constitute a part of this specification, illustrate the utility model and together with the description serve to explain, without limitation, the utility model. In the drawings:
FIG. 1 is a schematic diagram of a deodorizing system according to an embodiment of the present utility model when performing dust removal, desulfurization and VOCs removal processes;
FIG. 2 is a schematic diagram of a deodorizing system according to an embodiment of the present utility model, when a zeolite molecular sieve desorption process is performed;
Fig. 3 is a schematic diagram of a heat exchange unit according to an embodiment of the present utility model.
Reference numerals illustrate:
S2 dust collector S21 primary filter screen
S22 medium-efficiency filter bag S3 desulfurizing device
S31 solid desulfurizing agent S4 VOCs processing unit
S41 upstream flow distribution cavity S42 molecular sieve filling cavity
S43 downstream flow distribution cavity S44 first heat exchange structure
S51 adsorption fan S52 desorption fan
S53 compressor S71 preheating device
S72 heating device S8 tail end processing device
S9 expansion valve
Detailed Description
The following describes the detailed implementation of the embodiments of the present utility model with reference to the drawings. It should be understood that the detailed description and specific examples, while indicating and illustrating the utility model, are not intended to limit the utility model.
It should be noted that, without conflict, the embodiments of the present utility model and features of the embodiments may be combined with each other.
The utility model will be described in detail below with reference to the drawings in connection with exemplary embodiments.
Referring to fig. 1 and 2, a first exemplary embodiment of the present utility model provides a deodorizing system including a dust removing unit S2, a desulfurizing unit S3, a VOCs treating unit, a purifying line, and a waste discharging line.
Specifically, dust collector S2 is arranged in the dust in desorption foul smell, and desulfurization device S3 is arranged in the hydrogen sulfide in the desorption foul smell, and VOCs handles the assembly and is arranged in the VOCs in the desorption foul smell. Because the nasal-olfactory threshold of ammonia is about 378ug/m 3, and the concentration of ammonia in the odor in the garbage station is generally below 200ug/m 3, the ammonia in the garbage station has no odor-causing capability basically and can not be specially treated.
The VOCs treatment assembly specifically comprises a VOCs treatment unit S4, an adsorption fan S51, a desorption fan S52, a heating device S72, an end treatment device S8 and a heat exchange unit. The VOCs treatment unit S4 comprises a zeolite molecular sieve capable of removing VOCs in odor, and the zeolite molecular sieve has strong adsorption capacity for both water-soluble VOCs and non-water-soluble VOCs.
The flow of removing dust, hydrogen sulfide, water-soluble VOCs and water-insoluble VOCs in odor by the deodorizing system can refer to fig. 1, and during practical application, the purifying pipeline can be connected in series with the dust removing device S2, the desulfurizing device S3 and the VOCs processing unit S4 along the direction from the upstream end (i.e. the odor input end) to the downstream end (the purified gas output end) of the purifying pipeline, meanwhile, the purifying pipeline is also connected in series with the adsorption fan S51, and the adsorption fan S51 can be arranged between the VOCs processing unit S4 and the purified gas output end as shown in fig. 1, but can also be arranged at other positions, such as being close to the odor input end.
Under the drive of the adsorption fan S51, the odor entering the purifying pipeline from the odor input end can sequentially pass through the dust removing device S2, the desulfurizing device S3 and the VOCs treatment unit S4, so that dust, hydrogen sulfide, water-soluble VOCs and water-insoluble VOCs are sequentially removed, and the purified odor is discharged out of the purifying pipeline through the purified gas output end. The flow path of the odor in the purge line can be referred to as S11-S15 in fig. 1.
When the zeolite molecular sieve reaches an adsorption saturation state, the zeolite molecular sieve can not adsorb more VOCs, so that in order to ensure that the zeolite molecular sieve can be repeatedly used, the zeolite molecular sieve also needs to be subjected to desorption and regeneration at regular or irregular intervals. In the present exemplary embodiment, desorption and regeneration of the zeolite molecular sieve are achieved in combination with a waste discharge line.
Specifically, the exhaust line may be connected in series with the heating device S72, the VOCs processing unit S4, and the terminal processing device S8 in the direction from the upstream end (i.e., the desorption gas input end) to the downstream end (i.e., the desorption gas output end) thereof, and at the same time, the exhaust line may also be connected in series with the desorption fan S52, and the desorption fan S52 may be disposed between the VOCs processing unit S4 and the terminal processing device S8 as shown in fig. 2, but may also be disposed at other positions, such as being disposed close to the desorption gas input end.
Under the drive of the desorption fan S52, the desorption gas (such as clean air) entering the waste discharge pipeline from the desorption gas input end can sequentially pass through the heating device S72, the VOCs treatment unit S4 and the tail end treatment device S8, wherein the desorption gas can be heated to be high-temperature desorption gas after passing through the heating device S72, the high-temperature desorption gas can exchange heat with the zeolite molecular sieve when passing through the VOCs treatment unit S4, the adsorption capacity of the zeolite molecular sieve is reduced after the temperature of the zeolite molecular sieve rises, so that the VOCs are desorbed from the zeolite molecular sieve to further flow to the tail end treatment device S8 along with the desorption gas, the desorption gas entering the tail end treatment device S8 contains high-concentration VOCs, the concentrated purification treatment is more convenient, and the desorption gas discharged from the tail end treatment device S8 accords with the emission standard, and can be directly discharged to the atmosphere through the desorption gas output end. The flow path of the desorption gas in the exhaust line can be referred to as S61-S66 in fig. 2.
After the zeolite molecular sieve is heated to desorb VOCs, the zeolite molecular sieve is required to be cooled through a heat exchange unit in the VOCs treatment assembly to recover the state of the adsorbed VOCs, so that the regeneration of the zeolite molecular sieve is realized.
It can be seen that the deodorizing system according to this exemplary embodiment processes the odor in the form of the dust removing device S2, the desulfurizing device S3, and the VOCs processing assembly containing zeolite molecular sieve, which are matched with the purifying pipeline and the waste discharging pipeline, wherein the dust removing device S2 and the desulfurizing device S3 can remove the dust and the hydrogen sulfide in the odor, respectively, the zeolite molecular sieve in the VOCs processing assembly can efficiently remove the water-soluble and water-insoluble components in the odor, and especially, the processing efficiency of the water-insoluble components is greatly improved compared with that of the conventional deodorizing process, so that the emission concentration of the odor can be greatly reduced. And the adsorption, desorption and regeneration of the zeolite molecular sieve can be realized by matching with other parts, a purification pipeline and a waste discharge pipeline in the VOCs treatment assembly such as a heat exchange unit, so that the deodorizing system can be ensured to stably deodorize for a long time.
In one embodiment, referring to FIG. 1, the VOCs treatment unit S4 may further comprise an upstream flow distribution chamber S41, a molecular sieve loading chamber S42, and a downstream flow distribution chamber S43 in sequential airflow communication, the molecular sieve loading chamber S42 being loaded with zeolite molecular sieve. By providing the upstream flow distribution chamber S41 and the downstream flow distribution chamber S43, the airflow rate input into the molecular sieve filling chamber S42 and the airflow rate output from the downstream flow distribution chamber S43 can be reasonably distributed, thereby improving the adaptability of the deodorizing system.
In one embodiment, the VOCs treatment assembly may be provided with a plurality of the aforementioned VOCs treatment units S4, and the plurality of VOCs treatment units S4 are disposed in parallel in both the purge line and the waste discharge line. So, when purifying pipeline or discharging pipeline during operation, all can branch into multistage little amount of wind air current with the big amount of wind air current in the pipeline through the bleeder pipeline, the little amount of wind air current of multistage is handled to rethread a plurality of VOCs processing unit S4 one-to-one, both can promote absorption, desorption effect, can realize the absorption, the desorption of low-cost and low-traffic again.
In one embodiment, referring to FIG. 3, a heat exchange unit in a VOCs treatment assembly may include a heat exchange medium and a first heat exchange structure S44, a compressor S53, a second heat exchange structure, and an expansion valve S9 connected in a closed loop by piping for circulating the heat exchange medium. The first heat exchange structure S44 is in heat exchange contact with the zeolite molecular sieve and can cool the zeolite molecular sieve after desorption and temperature rise, and the second heat exchange structure is formed as a preheating device S71 connected in series in the waste discharge pipeline and positioned at the upstream of the heating device S72.
Through the arrangement of the embodiment, not only the zeolite molecular sieve with the temperature raised by desorption can be cooled, but also the part of waste heat of the zeolite molecular sieve can be recycled, and the desorption gas is preheated before being heated, so that the energy consumption of the heating device S72 is reduced. The specific flow of the waste heat recovery and utilization is as follows:
The low-pressure low-temperature liquid-phase medium in the first heat exchange structure S44 is converted into a high-pressure high-temperature gas-phase medium by absorbing the residual heat in the zeolite molecular sieve with the temperature raised by desorption;
The low-pressure high-temperature gas-phase medium is pressurized by the compressor S53 and is converted into a high-pressure high-temperature gas-phase medium;
The high-pressure high-temperature gas phase medium enters a preheating device S71 (namely a second heat exchange structure) to preheat desorption gas, and the high-pressure high-temperature gas phase medium is converted into a high-pressure low-temperature liquid phase medium after heat exchange;
the high-pressure low-temperature liquid-phase medium is expanded and depressurized in an expansion valve S9, converted into the low-pressure low-temperature liquid-phase medium and then flows back to the first heat exchange structure S44; so far, the primary waste heat recovery cycle of the heat exchange medium is completed.
In one embodiment, the first heat exchange structure S44 may include a pre-buried heat exchange tube at least partially pre-buried in the zeolite molecular sieve, and exchanges heat with the zeolite molecular sieve through contact between the tube wall and the zeolite molecular sieve, so that the heat exchange efficiency is high, and the structure is simple and compact.
In the prior art, the downstream of the biological filter is also generally provided with an adsorption device filled with activated carbon or chemical filter materials to further reduce the concentration of odor discharged from the tail end, but the activated carbon is in danger of waste after adsorption, and special treatment is required, and the chemical filter materials have higher cost and difficult popularization.
The deodorizing system according to the present exemplary embodiment can realize that no waste water or hazardous waste solid is produced in the whole deodorizing process by the following embodiments.
In one embodiment, the desulfurization device S3 is filled with a solid desulfurizing agent S31; and/or the dust removing device S2 is provided with a multi-layer filtering structure. So set up, deodorization, desulfurization, the three major links of taking off VOCs among the deodorization system, all do not have waste water to produce, and the feature of environmental protection is good. For example, the solid desulfurizing agent S31 can be an iron oxide desulfurizing agent, the active component of the iron oxide desulfurizing agent is iron oxide, the adsorption capacity is large, the cost is low, the solid desulfurizing agent S31 has higher removal capacity for hydrogen sulfide, and the main component of the solid desulfurizing agent S31 is iron sulfide after saturated adsorption, does not belong to hazardous waste, and can be subjected to harmless treatment. The multi-layer filtering structure can adopt the primary filter screen S21 and the medium-effect filter bag S22 which are arranged in a layered manner, so that the cost is low, and the dust removal effect is good.
In addition, the tail end treatment device S8 can adopt a regenerative oxidation furnace, so that the VOCs in the desorption gas can be effectively guaranteed to be thoroughly oxidized and destroyed, and waste water and dangerous waste solid substances are not generated in the process.
In one embodiment, the regenerative oxidation furnace may be a ERTO furnace with electrical heating as a heat source; and/or the heating device S72 is an electric heater, so that the deodorizing system is more energy-saving and environment-friendly.
In addition, the second exemplary embodiment of the present utility model also provides a garbage station, which includes the deodorizing system, so that all technical effects brought by the deodorizing system are provided, and are not described herein.
The foregoing details of the optional implementation of the embodiment of the present utility model have been described in conjunction with the accompanying drawings, but the embodiment of the present utility model is not limited to the specific details of the foregoing implementation, and various simple modifications may be made to the technical solution of the embodiment of the present utility model within the scope of the technical concept of the embodiment of the present utility model, where all the simple modifications belong to the protection scope of the embodiment of the present utility model.
In addition, the specific features described in the foregoing embodiments may be combined in any suitable manner, and in order to avoid unnecessary repetition, various possible combinations are not described further.
In addition, any combination of various embodiments of the present utility model may be performed, so long as the concept of the embodiments of the present utility model is not violated, and the disclosure of the embodiments of the present utility model should also be considered.
Claims (10)
1. A deodorizing system, characterized in that it comprises:
The dust removing device (S2) and the desulfurizing device (S3) are respectively used for removing dust and hydrogen sulfide of odor;
The VOCs treatment assembly comprises a VOCs treatment unit (S4), an adsorption fan (S51), a desorption fan (S52), a heating device (S72), a tail end treatment device (S8) and a heat exchange unit, wherein the VOCs treatment unit (S4) comprises a zeolite molecular sieve capable of removing VOCs in odor, and the heat exchange unit can cool the zeolite molecular sieve after desorption and temperature rise;
The purification pipeline is connected with the dust removing device (S2), the desulfurizing device (S3) and the VOCs treatment unit (S4) in series along the direction from the upstream end to the downstream end, the purification pipeline is also connected with the adsorption fan (S51) in series, the upstream end of the purification pipeline is an odor input end, and the downstream end of the purification pipeline is a purified gas output end;
The waste discharge pipeline is connected in series with the heating device (S72), the VOCs treatment unit (S4) and the tail end treatment device (S8) along the direction from the upstream end to the downstream end, the waste discharge pipeline is also connected in series with the desorption fan (S52), and the upstream end of the waste discharge pipeline is a desorption gas input end and the downstream end is a desorption gas output end.
2. The deodorizing system as set forth in claim 1, wherein said VOCs treatment unit (S4) further comprises an upstream flow distribution chamber (S41), a molecular sieve packing chamber (S42) and a downstream flow distribution chamber (S43) in sequential airflow communication, said molecular sieve packing chamber (S42) being filled with said zeolite molecular sieve.
3. The deodorizing system as set forth in claim 1, wherein said VOCs treatment assembly is provided therein with a plurality of said VOCs treatment units (S4), and a plurality of said VOCs treatment units (S4) are disposed in parallel in both said purifying pipe and said waste discharging pipe.
4. The deodorizing system as set forth in claim 1, characterized in that said heat exchange unit comprises a heat exchange medium and a first heat exchange structure (S44), a compressor (S53), a second heat exchange structure and an expansion valve (S9) connected in a closed loop by a pipe for circulating said heat exchange medium;
The first heat exchange structure (S44) is in heat exchange contact with the zeolite molecular sieve and can cool the zeolite molecular sieve after desorption and temperature rise, and the second heat exchange structure is formed as a preheating device (S71) which is connected in series in the waste discharge pipeline and is positioned at the upstream of the heating device (S72).
5. The deodorizing system as set forth in claim 4, characterized in that said first heat exchange structure (S44) comprises pre-buried heat exchange tubes, which are at least partially pre-buried in said zeolite molecular sieve.
6. The deodorizing system according to claim 1, characterized in that said desulfurizing device (S3) is filled with a solid desulfurizing agent (S31); and/or the dust removing device (S2) is provided with a multi-layer filtering structure.
7. The deodorizing system as set forth in claim 6, characterized in that said solid desulfurizing agent (S31) comprises an iron oxide desulfurizing agent, and said multi-layer filtering structure comprises a primary filter screen (S21) and a middle-effect filter bag (S22) arranged in layers with each other.
8. The deodorizing system as claimed in claim 1, characterized in that said heating means (S72) are electric heaters; and/or the end treatment device (S8) is a regenerative oxidation furnace using electric heating as a heat source.
9. The deodorizing system as set forth in claim 1, characterized in that said adsorption fan (S51) is disposed between said VOCs processing unit (S4) and said purge gas output; and/or the desorption fan (S52) is disposed between the VOCs processing unit (S4) and the end processing apparatus (S8).
10. A waste station, characterized in that it comprises a deodorizing system according to any one of claims 1 to 9.
Priority Applications (1)
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CN202323102284.9U CN221514003U (en) | 2023-11-16 | 2023-11-16 | Deodorization system and garbage station |
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CN202323102284.9U CN221514003U (en) | 2023-11-16 | 2023-11-16 | Deodorization system and garbage station |
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CN221514003U true CN221514003U (en) | 2024-08-13 |
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CN202323102284.9U Active CN221514003U (en) | 2023-11-16 | 2023-11-16 | Deodorization system and garbage station |
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CN (1) | CN221514003U (en) |
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2023
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