KR101600074B1 - Apparatus and method for manufacturing multiple odor absorbents - Google Patents
Apparatus and method for manufacturing multiple odor absorbents Download PDFInfo
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- KR101600074B1 KR101600074B1 KR1020150117179A KR20150117179A KR101600074B1 KR 101600074 B1 KR101600074 B1 KR 101600074B1 KR 1020150117179 A KR1020150117179 A KR 1020150117179A KR 20150117179 A KR20150117179 A KR 20150117179A KR 101600074 B1 KR101600074 B1 KR 101600074B1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3078—Thermal treatment, e.g. calcining or pyrolizing
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2/00—Processes or devices for granulating materials, e.g. fertilisers in general; Rendering particulate materials free flowing in general, e.g. making them hydrophobic
- B01J2/12—Processes or devices for granulating materials, e.g. fertilisers in general; Rendering particulate materials free flowing in general, e.g. making them hydrophobic in rotating drums
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/16—Alumino-silicates
- B01J20/165—Natural alumino-silicates, e.g. zeolites
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
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Abstract
The present invention relates to a device for producing a granular composite odor adsorbent and a method for producing a complex odor adsorbent using the same, wherein the composite odor adsorbent is composed of ammonia, trimethylamine and the like, which are generated from food waste and cause odor, It has an excellent effect in adsorbing and removing hydrogen sulfide and methyl mercaptan. In addition, in the production of the composite odor adsorbent, a granular raw material having a uniform and high density can be formed through a molding apparatus, granular raw materials can be produced in a large capacity by continuous molding, It is possible to prevent the granular form breakage and to prevent the clogging of the screen by drying only the fine powder after drying the surface and the fine powder in the drying and firing apparatus and to burn the granular raw material in which the fine powder is removed at the time of firing It eliminates the rotation resistance caused by the differential and improves the product quality through efficient firing and has energy saving effect.
Description
The present invention relates to an apparatus for producing a complex odor adsorbent and a method for producing a complex odor sorbent using the same, and more particularly, to a method for producing a complex odor sorbent by mixing natural zeolite, ash, yellow earth, bentonite, sodium hydrogencarbonate, And a method for producing a complex odor adsorbent using the same.
Recently, due to changes in the perception of environmental rights, odor problems are becoming serious as well as air pollution. Since Korea has a mixed population of residential area and industrial area for efficient use of the limited land area, the incidence of odor complaints is very high due to high population density, and there are many difficulties in efficient management due to the variety of types and sources of odorous substances .
In addition to the large number of substances causing these odors, it is difficult to uniformly express the extent of the damage or the degree of damage due to the complex action of odorous substances or individual differences in the smell, which is the most difficult and difficult to solve It is considered to be one of the problems. Odor is one of the sensory pollution causing mental and psychological damage rather than the harmfulness to the human body. Recently, the quality of life and environmental consciousness have improved, and civil complaints are increasing every year. The damage caused by the odor is mainly limited to the vicinity of the source, but it can affect far distances depending on the weather conditions, such as wind direction, wind speed, and temperature inversion, as well as the local features of the area.
In Korea, the amount of food waste generated due to the traditional food culture has raised the need for management measures. Among them, we are trying to use food waste as a resource as much as possible.
Food waste is discharged every day from households and restaurants. The amount of such garbage is gradually increasing from 13,672 tons / day in 2010 to 13,537 tons / day in 2011 and 13,209 tons / day in 2012. Food waste It has a different composition and content, and its protein content is relatively high in terms of nutrient composition. It has a useful value as feed and compost, but it has a high water content and is easily corrupted and malodorous. Therefore, when disposing of food waste, damage is increasing due to odor such as incessant complaints around environment basic facility due to odor generated.
Food waste recycling facilities, one of the abovementioned environmental facilities, have introduced waste disposal agents since 1995 and the amount of food waste has been rapidly increasing due to the separation and discharge of food waste mixed and discharged into the standard bags. It started to be installed in the room. However, this food waste disposal facility has been recognized as a disgusting facility due to the severe odor generated during transportation and processing of food waste, and it has become a subject of complaints of residents in the surrounding area, resulting in NIMBY ('Not In My BackYard') phenomenon. In the process, malodorous substances such as mercaptans, amines and the like are generated, causing discomfort and disgust to the residents in the surrounding area, making them subject to collective complaints, and it is difficult to install and operate a food waste recycling facility.
Patent Document 1 discloses a method of adsorbing an alkaline gas such as ammonia (NH 4 ), an acid gas such as hydrogen sulfide (H 2 S), etc. at the same time, Since the malodor gas adsorbed at a low temperature of about 200 ° C. after the malodorous gas is sufficiently adsorbed can be regenerated by oxidative decomposition or desorption, it is possible to continuously use the malodorous gas-adsorbed oxidative decomposition and its manufacturing method have.
However, in order to form the adsorbent in the form of granules, it is troublesome to dry only the granules in the form of granules, to separate only the granules through the screen, and to transfer the remaining powder back to the molding machine. In order to increase the density of the granules, Since the process must be stopped and additional raw materials should not be added, the process must be operated in a bath type and the granules generated after the molding process must be dried and calcined together with the unnecessary energy There is a problem that it is consumed.
In the present invention, an adsorbent containing natural zeolite, ash, loess, bentonite and sodium hydrogencarbonate is prepared in order to remove the odor generated from food waste, and thereby, mercaptan such as ammonia, trimethylamine, The adsorbent of the present invention is capable of adsorbing odor and removing odor in a complex manner.
In addition, it is possible to form granules continuously in the granular form at the time of manufacturing the granular raw material, thereby making it possible to produce a large-capacity granular adsorbent, no separate powder separation process is required, and the angle of the molding device can be easily controlled To provide an apparatus for producing a complex odor adsorbent having excellent energy efficiency by producing a uniform and high-density granular raw material through a molding apparatus, drying only the surface of the granular raw material, and then separating the fine powder to prepare an adsorbent do.
According to an aspect of the present invention, there is provided a raw material mixing apparatus (100) for mixing and uniformly supplying a raw material; A forming
The
The
The screening and crushing
Another embodiment of the present invention is a process for producing a raw material mixture comprising: a raw material mixing step of uniformly mixing raw materials including natural zeolite, Ash, loess, bentonite and sodium hydrogencarbonate (NaHCO3); Molding the mixed raw material into a granule form through a
Preferably, 20 to 25 parts by weight of ash, 4 to 7 parts by weight of loess, 1 to 3 parts by weight of bentonite and 13 to 16 parts by weight of sodium hydrogencarbonate are uniformly mixed with 100 parts by weight of natural zeolite Do.
delete
The present invention relates to an apparatus for producing a complex odor adsorbent and a method for producing a complex odor sorbent using the same, wherein the complex odor sorbent comprises ammonia, trimethylamine, and the like, which are generated from food waste, There is an excellent effect to adsorb and remove methyl mercaptan.
In addition, in the production of the composite odor adsorbent, a granular raw material having a uniform and high density can be formed through a molding apparatus, and granular raw materials can be produced in a large capacity by continuous molding. Further, only the granular raw material having a size larger than the reference size is discharged to the outside, so that a separate powder separation process is not required, and the granular raw material having a predetermined size or more is separated from the powder raw material, The granular adsorbent can be produced.
The granule type raw material is dried and fired in a drying and firing apparatus to separate only fine powder to prevent breakage of the granule type and to prevent clogging of the screen. In firing, granule type raw material It is possible to reduce the rotational resistance caused by the fine powder and improve the quality of the product through efficient firing and to save energy.
1 is a schematic view schematically showing an apparatus for producing a complex odor adsorbent of the present invention.
2 is a schematic diagram schematically showing a molding apparatus according to an embodiment of the present invention.
3 is a schematic view schematically showing the molding principle of a molding apparatus according to an embodiment of the present invention.
4 is a schematic view schematically showing a drying and firing apparatus according to an embodiment of the present invention.
FIG. 5 is a schematic view showing the particle state of granular raw material and fine powder while passing through the drying and firing apparatus according to an embodiment of the present invention.
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The preferred embodiments of the present invention will now be described in detail with reference to the accompanying drawings. Hereinafter, preferred embodiments of the present invention will be described in detail with reference to the accompanying drawings. As well as the fact that
Throughout this specification, when a member is "on " another member, this includes not only when the member is in contact with another member, but also when there is another member between the two members.
Throughout this specification, when an element is referred to as "including" an element, it is understood that it may include other elements as well, without departing from the other elements unless specifically stated otherwise.
In each step, the identification code is used for convenience of explanation, and the identification code does not describe the order of the steps, and each step may be performed differently from the stated order unless clearly specified in the context. have. That is, each of the steps may be performed in the same order as the specified order, substantially simultaneously or in the opposite order.
Also, throughout this specification, the reference size means a predetermined arbitrary size and can be changed as needed in the production of the adsorbent.
Hereinafter, preferred embodiments of the present invention will be described in detail with reference to the drawings.
FIG. 1 is a schematic view schematically showing an apparatus for producing a complex odor adsorbent according to an embodiment of the present invention. The apparatus for producing a complex odor adsorbent includes a raw
The raw
The raw materials mixed in the raw
More specifically, the rotating
The
Generally, the
The
A
The height of the
The
And a
The injection nozzle of the
The
A bypass line is further provided when the solenoid valve for controlling the injection amount of the
The number of revolutions of the
The angle of the
Specifically, the drying and firing
The cylindrical rotary dryer constituting the drying and firing
The
The drying
Accordingly, the firing
In addition, since fine particles are removed in the middle of the drying and firing
Referring to the drying and firing
The hood has a sealing device between the hood and the rotating body so as to block the inflow of outside air. The inlet hood, the outlet hood and the intermediate hood may each include a sealing device. The inlet and outlet are formed in the inlet hood and the outlet hood, respectively, and a differential outlet is formed in the intermediate hood.
Preferably, the charging unit is provided on an inclined upper portion of a cylindrical rotary dryer, which is a place where the granular material to be dried is input to the rotary dryer.
Preferably, the discharge unit is provided at an inclined lower portion of an inclined cylindrical rotary dryer for discharging the adsorbent produced by firing by the
The differential discharge unit collects the fine particles discharged from the perforation hole of the cylindrical rotating screen and discharges the discharged fine particles to the outside. The differential discharge unit is also formed into a hopper shape, and a rotary valve or a double gate is installed, Is prevented from leaking. The conveyor for discharging the adsorbent and the conveyer for discharging the fine particles may be disposed at a lower portion of the discharge portion and a conveyor for discharging the granular material, respectively, A belt conveyor, a screw conveyor, a chain conveyor, or the like may be used.
At this time, the fine particles separated and discharged from the differential discharge conveyor can be transferred to the
The inlet hood or the outlet hood is formed with an exhaust port and the air introduced through the air supply device is heated by hot air by the hot
Since the cooled air and the evaporated water vapor used for drying and firing may include dust, it is preferable to connect the exhaust duct to the exhaust port and further purify the exhaust duct by including a dust filter bag. To the atmosphere.
When the hot
The hot
The granular adsorbent produced through the drying and
On the other hand, a raw material mixing step of uniformly mixing raw materials including natural zeolite, ash and additives, a step of molding the mixed raw material into a granule shape through a
The raw material mixing step is a step of uniformly mixing raw materials including natural zeolite, ash, loess, bentonite and sodium hydrogencarbonate, preferably 20 to 25 parts by weight of ash, 4 to 7 parts by weight of loess 1 to 3 parts by weight of bentonite, and 13 to 16 parts by weight of sodium hydrogencarbonate.
The natural zeolite is a natural mineral having various physico-chemical properties which are industrially useful because of a pore structure peculiar to the surface pore existing in the crystal. The natural zeolite has a structure of Si , Al) O 4 Tectosilicates are structured in three dimensions, with all the oxygen atoms in the tetrahedron being shared by another tetrahedron. Also, the natural zeolite has a lattice structure (specific gravity: 2.0-2.3) which is large enough to form a large pore size of 2.3-7.5 Å in the crystal within the crystal, and the size of the pore is 4-12 The oxygen is determined by the shape of the oxygen ring at the entrance to the structural pore and by the number of intervening oxygen.
In particular, natural zeolites are collected in the form of "zeolitic tuff", which is mostly degraded to fine-grained tuff, and is a hydrated silicate containing a small amount of Na, K, Ca, Mg, As minerals, the types are clinoptilolite, mordenite, heulandite, phillipsite, erionite, chabazite and periorite ferrierite and the like. In the present invention, the type of natural zeolite is not particularly limited, and natural zeolite collected from nature can be selectively used.
The fly ash has a large specific surface area and a large number of pores, and thus has good adsorption power, reduces hydration heat, and is economical because it can lower the unit cost of the adsorbent including the ash in terms of recycling waste materials. In addition, there is an excellent effect in increasing the porosity, improving the melting point, and lightening the weight of the composite odor adsorbent. The ash is preferably contained in an amount of 20 to 25 parts by weight of ash relative to 100 parts by weight of natural zeolite in the composite odor adsorbent using mixed zeolite. If the amount is less than 20 parts by weight or more than 25 parts by weight, . In addition, the particle size of the ash can be used without particular proposal if the particle size is such that the compound odor adsorbent does not cause problems in moldability during production.
Yellow loess is a weakly alkaline soil collected from the lower layer of the ground, which is different from the normal surface layer. It is rich in calcium carbonate and consists of various mineral particles such as quartz, feldspar, mica and calcite. It is also known that loess is chemically composed of silica, iron, alumina, magnesium, sodium, potassium, lime, smectite, etc., emitting far infrared rays, generating oxygen and deodorizing function. And the strength of the adsorbent is increased by lowering the melting point in the production of the composite odor adsorbent including the yellow loess.
The particle size of the loess is not particularly limited as long as it does not cause problems in the moldability of the adsorbent, but preferably a particle size of 0.02 to 0.05 mm can be used. The yellow loess of the present invention may be contained in an amount of 4 to 7 parts by weight based on 100 parts by weight of the natural zeolite. If the yellow loess component is less than 4 parts by weight, it is difficult to expect a far-infrared radiation and deodorizing effect. There is a problem that the moldability of the resin composition decreases.
Bentonite is a volcanic ash and rhyolite of the Neogene period, which is formed by stratification of volcanic rocks of Pelvic volcanism (rock formation) and formed stratification. The bentonite is composed of Montmorilllite-based expansive three- Si), and it can be expressed as Al 2 Si 4 (OH), which is a chemical structure of pyrophylite. In addition, the bentonite is gelled due to its swelling property by water in powder state. When the compounded zeolite is incorporated in the mixed zeolite adsorbent using the mixed zeolite of the present invention, the natural zeolite, fly ash, loess, bentonite, sodium hydrogencarbonate NaHCO 3 ) and the organic binder to maintain the shape of the formed adsorbent to prevent deformation.
The bentonite is preferably contained in an amount of 1 to 3 parts by weight based on 100 parts by weight of the natural zeolite. When the amount of the bentonite is less than 1 part by weight, the strength of the adsorbent is lowered and the granule shape is easily broken. .
Sodium hydrogencarbonate generates pores or pores due to the generation of HCO 3 gas during decomposition by heat during drying, and Na + in the inorganic system remains in the adsorbent even after firing, and can help form a structural force. In addition, natural zeolite, ash, loess, and bentonite can be adhered or adhered to the adsorbent of the present invention in the process of forming the pores or pores. The sodium hydrogencarbonate is preferably contained in an amount of 13 to 16 parts by weight based on 100 parts by weight of the natural zeolite. When the amount is less than 13 parts by weight, the desired structural force can not be imparted to the adsorbent. There may be a problem that the strength is excessively deteriorated.
The step of shaping the mixed raw material into a granule form through a molding apparatus includes a step of molding granules while rotating the raw materials and the binder mixed in the rotating body and preferably 100 parts by weight of the mixed raw materials 1 to 5 parts by weight of an organic binder may be contained and granulated through a molding apparatus.
The organic binder enhances the bonding strength between the mixed raw materials and improves the adhesion force to grow granules. The organic binder is composed of carbon, hydrogen, and oxygen as chemical components. In addition, inorganic binders such as sodium, magnesium, calcium, . As the organic binder, it is preferable to use at least one of molasses and carboxy methyl cellulose, and it may be a mixture of molasses and carboxymethyl cellulose, It can also be used. Preferably, the organic binder may be used by mixing water and molasses in a ratio of 1: 1 to 3: 1.
The amount of the organic binder is preferably 1 to 5 parts by weight based on 100 parts by weight of the mixture. If the amount of the organic binder is less than 1 part by weight, porosity may be insufficient due to oxidation of organic materials during firing, A problem may arise in which the adhesive strength is lowered and the shape of the adsorbent can not be maintained.
In the molding step, when the raw materials mixed in the rotating body and the organic binder are aggregated while rotating and the mixed raw materials in the form of powder are grown into granules, the centrifugal force due to the rotation causes the frictional resistance and gravity resistance The mixed raw material in the form of relatively small particles and powder is moved to the upper side and discharged to the outside of the rotating body so that only the granular raw material having the standard size or more can be obtained. Since the time required for the mixed raw material in the powder form to grow in the form of granules is very short, the density of the granular raw material is low, the strength is not rigid and the specific gravity can be lightened. The granules can be further rotated inside the rotating body even after the growth, so that it becomes possible to obtain a dense and hard granular raw material through rolling friction.
The drying and firing step may include a drying step of applying heat to the granular raw material, a drying step of removing heat from the granular surface by applying heat to the granular raw material, A fine particle removing step of passing fine particles through a rotating screen including a hole, and a sintering step of applying heat to the raw material from which the fine particles have been removed to obtain a sintered granular adsorbent.
Referring to FIG. 5, after a granular raw material and a fine powder are mixed in a cylindrical rotary dryer, the mixture is dried to dry only the surface by applying heat, and then passed through a rotating screen including perforated holes to remove fine powder, An adsorbent can be produced.
The sintering step is a step of drying only the surface of the granular raw material by heating the cylindrical rotary dryer at 80 to 150 ° C in order to prevent the granular raw material from being broken, more preferably from 100 to 120 ° C It can be dried by applying heat. If the temperature of the drying step is out of the range of 80 to 150 ° C, the granular raw material may be broken or cracked and the quality may be deteriorated.
The granular raw material having the dried surface through the drying step is passed through a rotating screen including a perforated hole to remove fine particles, and the granular form mixture after the forming step is mixed with fine powders And unnecessary energy waste is generated in drying and firing granule particles. Therefore, it is preferable that the fine particles passing through the rotating screen including the perforated holes and excluding the granular raw material larger than the reference size are discharged to the outside, and only the granular raw material is transferred to the firing step and fired.
In the firing step, heat is applied to the granular raw material having undergone the fine powder elimination step, and as the firing step proceeds, moisture in the granular mixture is evaporated, and humidity or humidity increases in the air The evaporation of water vapor is further difficult to cause a phenomenon of adhesion between the particles of the granule type mixture or a phenomenon in which the granule type raw material is adhered to the inside of the apparatus. Therefore, the granular type raw material is directly subjected to hot- .
The calcining step is a step of adding an adsorbent to the granular raw material by applying hot air at a temperature of 250 to 800 ° C to produce an adsorbent. More preferably, the granular raw material is calcined by applying hot air at 450 to 600 ° C. If the material is fired at a temperature of less than 450 ° C, the inside of the granular material may not be properly fired so that the shape may not be maintained and may be flared or cracked. If fired at a temperature higher than 600 ° C, The zeolite may undergo phase transformation or phase collapse and adsorption performance may be deteriorated.
The granular raw material is heated in the drying step and the firing step so that the granular raw material can be slowly heated and dried, and the granular raw material is heated while being heated for a predetermined period of time, .
Only the granular raw material from which the fine particles have been removed in the firing step after the fine powder removing step can be fired so that the rotational resistance due to the fine powder can be eliminated and the firing can be efficiently performed because the number of revolutions of the granular raw material is increased. Therefore, the granular raw material to be finished is more round, harder and more improved in quality, and economical due to its lower volume and higher density.
In addition, it is possible to prevent the scattering of the fine particles in the workplace by eliminating the fine powder in advance before the firing step, thereby making the workplace clean and safe.
The granule-type adsorbent prepared through the above-described firing step may be subjected to a screening process in which only a predetermined size is selected in advance, and the adsorbent having a size smaller than the remaining standard is discharged to the outside, And granular adsorbents that do not meet the remaining 0.5 to 20 mm size can be crushed.
In the screening step, the adsorbent having a sub-standard size is pulverized into a powder form through a pulverizer, and the pulverized pulverized powder is introduced into a molding step together with the fine powder discharged in the pulverizing step, and then mixed with the raw materials mixed in the mixing step, And may be molded into an adsorbent.
Hereinafter, an embodiment of the present invention will be described. However, the scope of the present invention is not limited to the following preferred embodiments, and a person skilled in the art can carry out various modifications of the contents described in the present invention within the scope of the present invention.
[Experimental Example 1]
Raw materials containing NaHCO 3 in natural zeolite, ash, yellow soil and bentonite having the composition ratios shown in the following Table 1 were put into a raw
The organic binder was prepared by mixing water and molasses (33 wt%) at a ratio of 2: 1 at 30 캜.
A granule type raw material having a size of 0.5 to 20 mm was prepared at a ratio of 100 g of the starting material and 3.3 g of the organic binder in the ratio shown in Table 2 below using a molding machine.
The granular raw material was put into a dry calcining apparatus to prepare an adsorbent. The drying and firing apparatus was rotated for 30 minutes while maintaining the temperature within the range of 100-120 ° C. The fine powder contained in the granular raw material was removed through a rotating screen and then moved to the firing portion. The granular adsorbent prepared after sintering by hot air at a temperature of < RTI ID = 0.0 > 1 C < / RTI >
Examples 1 to 3 and Comparative Examples 1 to 4 were prepared by selecting only the particle size of the granules of 0.5 to 20 mm from the granular adsorbent through the screening crusher. The granule type adsorbent whose size did not satisfy 0.5 ~ 20 mm was crushed and re-transferred to the molding machine.
(unit :%)
(100)
(20)
(4)
(One)
(13)
(100)
(21.4)
(5.7)
(1.4)
(14.3)
(100)
(24.6)
(6.7)
(2.2)
(15.7)
(100)
(18.9)
(3.4)
(0.7)
(12.2)
(100)
(26.2)
(7.7)
(3.1)
(16.9)
(100)
(21.4)
(5.7)
(14.3)
(1.4)
(100)
(33.3)
(25)
(8.3)
(Unit: g, in parentheses) Weight portion )
[Experimental Example 2]
Performance evaluation according to drying temperature and firing temperature
In order to measure the maximum firing temperature at which the phase collapse of the zeolite does not occur during the production of the adsorbent through the experimental method of Experimental Example 1, the natural zeolite was subjected to an organic acid conversion Iodine adsorption performance was evaluated. The iodine adsorption performance was evaluated by weighing granular natural zeolite calcined in iodine solution for 24 hours.
Oxidation
Degree
absorption
Performance
Table 3 shows the results of the evaluation of the degree of organic matter oxidation and iodine adsorption performance at the firing temperature measured by the firing test. The firing efficiency was the highest at the firing temperature of 500 to 700 ° C., It was found that the adsorption function was reduced due to the clogging of the micropores due to the collapse of the structural defects inside the natural zeolite. Therefore, it was found that when the maximum firing temperature is 500 to 700 ° C., the adsorption efficiency is excellent.
According to the results of Table 3, the maximum firing temperature was set to 500 to 700 ° C., and the granular raw material, Example 1, was subjected to the four conditions of Table 4, Dried and calcined to prepare an adsorbent. The drying temperature was set to 80 to 150 ° C. The sintering temperature was set to 250 to 800 ° C while the total cumulative heating time was set to 90 minutes. Also, the experiment was carried out with a drying time> firing time for T1 or T2 and a firing time for T3 or T4.
(° C)
(min)
T1
T2
T4
The hydrophobic test was conducted on T1 to T4 prepared according to Table 4 to measure the release phenomenon against water. Experimental results showed that cracking or cracking of filter media occurred after firing and T1 and T3 showed water melting phenomenon in hydrophobic experiments. However, in case of T4, the strength was maintained and no cracking or cracking phenomenon could be observed. In the hydrophobic test, it was slightly dissolved in water but the shape did not change. Therefore, it was found that the drying temperature and the calcination temperature of the complex odor adsorbent using the mixed zeolite of the present invention are preferably 80 to 150 ° C. and 250 to 800 ° C., respectively.
Drying and firing equipment Energy consumption comparison
When 50 ton / hr of granular raw material prepared through the above Experimental Example 1 was fed into a desiccant using a drying apparatus having a capacity of 150 ton / hr, the amount of energy consumption of the prior art and the drying And the amount of energy consumption during the generation of the countercurrent hot air was compared at the part and the firing part.
The moisture content of the raw material charged into the dry calcining apparatus was 15%, and the residual moisture of the adsorbent was 4%.
(Kcal / hr)
3,825,000
3,060,000
273,000
(Kcal / hr)
2,250,000
1,800,000
90,000
(Kcal / hr)
8,893,500
4,042,500
1,347,500
(Kcal / hr)
879,200
329,700
329,700
(Kcal / hr)
4,435,200
3,158,400
-
(Kcal / hr)
20,282,900
12,390,200
2,040,200
From the results of Table 5, it can be seen that the energy saving amount according to the present invention corresponds to a total of 5,852,500 Kcal / hr (20,282,900- (12,390,200 + 2,040,200)). It can be seen that the energy saving ratio is about 28.85%.
[Experimental Example 3]
Iodine adsorption performance evaluation
Examples 1 to 3 and Comparative Examples 1 to 4 prepared in Experimental Example 1 were impregnated in an iodine solution for 24 hours, and weight and volume changes were measured.
From the results of Table 6, it can be seen that Examples 1 to 3 are superior in iodine adsorption performance to Comparative Examples 1 to 4. It was also confirmed that the adsorption performance of the complex odor adsorbents of Examples 1 to 3 was superior to that of the natural zeolite of Experimental Example 1 in comparison with the iodine adsorption performance evaluation.
[Experimental Example 4]
Evaluation of compressive strength
The compressive strength of each of Examples 1 to 3 and Comparative Examples 1 to 4 prepared in Experimental Example 1 and commercially available adsorbents DW1 to DW4 (KYOCERA CO., LTD.) Were measured after ten cycles each by using a compressive strength meter Respectively.
The results of Table 7 show that DW1 and DW2 which are commercially available products (600 to 1000 ° C) manufactured by high temperature baking are superior to those of Examples 1 to 3. However, DW3 to DW4 (200 to 600 ° C) The compressive strength was similar.
It was also confirmed that the compressive strength of Comparative Example 3 containing no sodium hydrogencarbonate and Comparative Example 4 containing starch were significantly lower than those of Examples 1 to 3 and Comparative Examples 1 and 2.
[Experimental Example 5]
Evaluation of adsorption performance of odor-inducing substances
10 g of each of the adsorbents DW1 to DW4 prepared in Examples 1 to 3 and Comparative Examples 1 to 4 prepared in Experimental Example 1 and commercially available adsorbents DW1 to 4 were sampled and injected into mercaptan, ammonia, acetaldehyde, and trimethylamine solutions as malodorous substances And the adsorption rate of the malodorous substance was measured by measuring the weight by time.
(Unit: g / g)
First, the adsorption performance against mercaptan, which is one of the odor inducing substances, was evaluated. As shown in Table 8, it was confirmed that Example 2 showed the highest adsorption efficiency at 0.420 g / g. Next, it was found that the adsorption efficiency was 0.396 g / g in the order of DW2 commercially available in Example 3 and 0.382 g / g.
(G / g)
Table 9 shows the results of the adsorption rate test using formaldehyde, which is one of the odor inducing substances, that 0.320 g / g was the best adsorption rate in Example 3, 0.314 g / g in Example 2, 0.310 g / g, and DW3 was 0.267 g / g.
(G / g)
Table 3 shows the results of adsorption experiments using ammonia among the odor-inducing substances. Example 2 showed the highest adsorption rate at 0.320 g / g, 0.318 g / g in Example 3, 0.310 g / g, and Comparative Example 4 was 0.280 g / g.
(G / g)
Table 11 shows the results of adsorption experiments using trimethylamine among the odor inducing substances. As a result of the adsorption test, the adsorption performance of Comparative Example 4 was 0.340 g / g, that of Example 2 was 0.307 g / g, that of Example 3 was 0.305 g / g, and Example 1 0.302 g / g.
The results of Tables 8 to 11 of Experimental Example 5 show that adsorption ratios of mercuric compounds such as mercaptan, formaldehyde, ammonia, and trimethylamine, which are malodorous substances, Example 3, Comparative Example 4 and DW2 showed a high adsorption rate. In Example 2, however, adsorption efficiency of mercaptan, formaldehyde, ammonia, and trimethylamine was comparatively evaluated, Respectively.
[Experimental Example 6]
Pilot - test Performance evaluation of adsorption tower
The adsorption experiment was conducted to evaluate the malodor removing performance of Example 2, which was rated excellent in Experimental Example 5 above.
A solution containing hydrogen sulfide, acetaldehyde, trimethylamine, and ammonia, which are major odor inducing substances generated in a food processing facility, is boiled in lukewarm water, and the gaseous phase gas is volatilized to a mixed odor absorbent Was passed through a packed bed to measure the outflow concentration after 2 hours and 4 hours.
(ppm)
As shown in Table 12, the ammonia concentration was measured to be 0.454 ppm and 1.937 ppm at the inlet concentration of 2.868 ppm after 2 hours and 4 hours, respectively, and the reduction rate was 84.2% and 32.4%, respectively. Acetaldehyde had an inlet concentration of 8.096 ppm , The reduction rate was measured as 98.4% and 87.7% at 0.133 ppm and 0.994 ppm after 2 hours and 4 hours, respectively, and trimethylamine was not detected at 0.159 ppm after 2 hours and 4 hours after the introduction at 1.434 ppm The reduction rate was measured as 88.9%.
The results of Experimental Examples 5 and 6 demonstrate that the complex odor adsorbent of the present invention can adsorb odor-causing substances such as ammonia, acetaldehyde, trimethylamine, mercaptan, etc., And it was confirmed that the efficiency of desorption by microwaves was excellent and the efficiency of regenerated energy was excellent.
The apparatus and method for producing a composite odor adsorbent according to the present invention are not limited to the above-described embodiments, and various modifications and changes may be made without departing from the spirit and scope of the present invention, The present invention is not limited to the scope of the claims of the present invention.
100: raw material mixing apparatus 150: raw material feeding apparatus
200: forming device
210: Rotor 211: Disc
212: dam part 213: loop part
220: drive device 230: lift means
250: scraper 260:
300: Drying and firing apparatus 310: Drying unit
320: differential separator 330: fired part
340: hot air generating part 350: adsorbent conveying device
400: Screen shredding device
Claims (9)
A forming device 200 for forming a granular material having a uniform size by rotating the mixed raw materials at different positions depending on the particle size,
A drying and firing apparatus 300 for removing fine powder contained in the granular raw material, drying and firing the powder to produce an adsorbent; And
And a screening and crushing apparatus 400 for screening only the predetermined size of the prepared adsorbent and then discharging the adsorbent having a size smaller than the remaining standard to the outside,
The drying and firing apparatus 300 includes:
And a differential separator (320) for separating the fine particles contained in the granular raw material in the cylindrical rotary dryer provided at a downward slope,
And the drying unit (310) and the burning unit (330) are divided around the differential separating unit (320).
The molding apparatus (200)
A rotating body 210 including a binder in the mixed raw material and rotating the mixed raw material in a granule shape while rotating the mixed raw material;
A jetting unit 260 disposed inside the rotating body 210 for jetting the binder;
A scraper 250 provided inside the rotating body 210 to rotate at different positions according to the size of the granule shape; And
And a control unit for controlling the number of revolutions and angle of the rotating body (210) or the injection time and injection amount of the injection unit (260).
The rotating body 210 is
An original plate 211 inclined;
A dam portion 212 formed perpendicularly to the rim of the circular plate 211 to prevent the granular material having a reference size or less from being discharged to the outside; And
And a loop part (213) provided at an upper end of the dam part (212) for rolling the granular raw material.
Wherein the differential separating unit (320) separates the fine particles contained in the granular raw material through a cylindrical rotating screen including a plurality of perforated holes.
The screening and crushing apparatus 400 includes a sorting unit for sorting the adsorbent into a predetermined size and discharging the adsorbent to the outside; And
And a crushing unit for crushing the adsorbent having a sub-standard size that has not passed through the sorting unit and delivering the crushed adsorbent to the granule forming apparatus 200.
Molding the mixed raw material into a granule form through a molding apparatus 200;
A drying and calcining step of drying and firing the granules-shaped raw material to produce an adsorbent;
And crushing the produced adsorbent by transferring the adsorbent to a screening crusher 400 to select only a predetermined size,
The drying and firing step comprises:
A drying step of applying heat to the granular shaped raw material to remove moisture on the granular surface;
A fine particle removing step of passing the raw material, which has been granulated through the drying step, through a rotating screen including a perforation hole to remove fine particles; And
And a calcining step of applying heat to the raw material from which the fine particles have been removed.
The raw material mixing step includes uniformly mixing 20 to 25 parts by weight of ash, 4 to 7 parts by weight of loess, 1 to 3 parts by weight of bentonite and 13 to 16 parts by weight of sodium hydrogen carbonate with respect to 100 parts by weight of natural zeolite By weight based on the total weight of the adsorbent.
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Citations (5)
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KR20010000418A (en) | 2000-09-27 | 2001-01-05 | 김대승 | Adsorption and deodorizing catalyst of malodors and a preparing method of the catalyst |
JP2003083677A (en) * | 2001-09-12 | 2003-03-19 | Shin Nihonkai Jukogyo Kk | Rotary dryer with cooler |
KR100456186B1 (en) * | 2001-06-12 | 2004-11-09 | 주식회사 얼라이브텍 | Eliminator Removing Nitrogen Oxides In Flue Gases And Method For Removing Nitrogen Oxides Thereby |
KR20100135209A (en) * | 2010-12-06 | 2010-12-24 | 이학섭 | Bio-soil for sewage using natural meterials and the manufacture method amd manufacture device |
KR101514433B1 (en) * | 2014-07-30 | 2015-04-24 | 동원엔지니어링(주) | Continuous Manufacture Machine of while the Granules Particle size is constant and the Dense solid |
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Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
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KR20010000418A (en) | 2000-09-27 | 2001-01-05 | 김대승 | Adsorption and deodorizing catalyst of malodors and a preparing method of the catalyst |
KR100456186B1 (en) * | 2001-06-12 | 2004-11-09 | 주식회사 얼라이브텍 | Eliminator Removing Nitrogen Oxides In Flue Gases And Method For Removing Nitrogen Oxides Thereby |
JP2003083677A (en) * | 2001-09-12 | 2003-03-19 | Shin Nihonkai Jukogyo Kk | Rotary dryer with cooler |
KR20100135209A (en) * | 2010-12-06 | 2010-12-24 | 이학섭 | Bio-soil for sewage using natural meterials and the manufacture method amd manufacture device |
KR101514433B1 (en) * | 2014-07-30 | 2015-04-24 | 동원엔지니어링(주) | Continuous Manufacture Machine of while the Granules Particle size is constant and the Dense solid |
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