TWM591007U - Structure of apparatus for disposal of kitchen waste - Google Patents

Structure of apparatus for disposal of kitchen waste Download PDF

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TWM591007U
TWM591007U TW108209856U TW108209856U TWM591007U TW M591007 U TWM591007 U TW M591007U TW 108209856 U TW108209856 U TW 108209856U TW 108209856 U TW108209856 U TW 108209856U TW M591007 U TWM591007 U TW M591007U
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disposal
kitchen waste
microorganisms
raw garbage
solid
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TW108209856U
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Chinese (zh)
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工藤隆彥
伊東久朋
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日商不鏽鋼藝術共榮有限公司
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Abstract

The present new model application is to solve the problems of conventional apparatus and method for disposal of kitchen waste, and to provide a method for disposal of kitchen waste that is capable of eliminating kitchen waste in a short time and being used stably for a long time. It is proposed a solution of using three types of microorganisms described in claim 1 as kitchen waste-decomposing microorganisms. The used microorganism is a bio-formulation formed by mixing with a porous spherical ceramic ([phi] 7 mm ~ [phi] 10 mm) and a cylindrical buffer material (inner diameter [phi] 10 mm * length 10 mm ~ 12 mm) which is made by resin. The bio-formulation formed by blending is mixed and grew with water and food waste. In addition, in the solid-phase treatment tank of the main body unit and the apparatus for disposal of kitchen waste, it is configured as a structure of which the hole diameter of mesh disposed at bottom of solid-phase treatment tank is set as [phi]1.5 mm ~ [phi]2.0 mm, the interval from the stirring blade is set as 10 mm ~ 30 mm, and a stirring blade which comprises a rubber disposed at the front end thereof and contacts with the mesh at the bottom of the solid-phase treatment tank is equipped with. By means of such a structure, a method for disposal of kitchen waste that can prevent from the problem of submersion and breakage of the mesh by water and can be used stably for a long time, is thereby provided.

Description

生垃圾處理機之構造Structure of the garbage disposal machine

本創作係關於一種使用芽孢桿菌(bacillus)屬微生物之生垃圾的處理方法。This creation is about a method of treating raw garbage using microorganisms belonging to the genus Bacillus.

以往,生垃圾(又稱為廚餘、食物垃圾、日常飲食廢棄物、或有機廢棄物),按照其處理方法可區分為「堆肥化方式」、「碳化方式」、「消滅化方式」等之種類;在其中,成為今日的主流的是一種稱為生物(bio)處理型的型式。該方式係一種利用微生物將生垃圾分解成水和二氧化碳的方式,按照其工程之不同可以區分為「堆肥型」和「消滅型」。「堆肥型」係一種以堆肥為生成物並加以排出的方式。又「消滅型」係一種將生垃圾最終形成水及CO 2並加以排出的方式。「堆肥型」型式的生垃圾處理機係必須瀝除生垃圾的水;由於生垃圾的水分多時就不能夠分解,因而將水分加以蒸發而使用於發酵。因此,需要花費高的消耗電力及燃料費。例如,在非專利文獻1中所記載之處理溫度為40℃至72℃。所以,其所使用的微生物也是使用耐熱性強的好氣性微生物及高溫性微生物。另一方面,在以往的消滅型型式的生垃圾處理機中,例如,如專利文獻1之記載所示,按照所使用之微生物的種類而定,也當然有必要將運轉溫度保持於高溫。又,為了防止篩網的阻塞,例如,可以使用如專利文獻2所示之附有發泡(bubbling)機構的裝置;例如,也可以使用如專利文獻3所示的將攪拌翼加以變形而成的裝置等。 <先前技術文獻> <專利文獻> In the past, raw waste (also known as kitchen waste, food waste, daily food waste, or organic waste) can be divided into "composting method", "carbonization method", "destruction method", etc. according to their disposal methods Type; among them, what has become the mainstream today is a type called bio (bio) treatment type. This method is a method that uses microorganisms to decompose raw waste into water and carbon dioxide, which can be divided into "compost type" and "extinction type" according to their engineering. "Compost" is a method that uses compost as a product and discharges it. The "extinction type" is a method of discharging raw garbage into water and CO 2 at the end. The "compost" type garbage disposal system must drain the water of the garbage; because the moisture of the garbage can not be decomposed for a long time, the water is evaporated and used for fermentation. Therefore, high power consumption and fuel costs are required. For example, the processing temperature described in Non-Patent Document 1 is 40°C to 72°C. Therefore, the microorganisms used are also aerobic microorganisms with high heat resistance and high-temperature microorganisms. On the other hand, in the conventional destruction type garbage disposal machine, for example, as described in Patent Document 1, it is of course necessary to maintain the operating temperature at a high temperature depending on the type of microorganism used. In addition, in order to prevent clogging of the screen, for example, a device with a bubbling mechanism as shown in Patent Document 2 may be used; for example, it may be formed by deforming a stirring wing as shown in Patent Document 3. Device etc. <Prior Art Documents><PatentDocuments>

<專利文獻1> 特開2001-316495(段落「0022」) <專利文獻2> 特開2000-37683(段落「0007」、圖3) <專利文獻3> 特開平11-128897 <非專利文獻> <Patent Document 1> Japanese Patent Laid-Open No. 2001-316495 (paragraph "0022") <Patent Document 2> Japanese Patent Laid-Open No. 2000-37683 (paragraph "0007", FIG. 3) <Patent Document 3> Japanese Patent Laid-Open No. 11-128897 <Non-patent literature>

<非專利文獻1> 田口文章、宗國富、張光磊著、「從熊貓分離出來的產生耐熱性酵素群之高溫細菌的生垃圾處理之試驗」、生物工學會誌、第79卷第12號、PP.463-469、2001年<Non-Patent Document 1> Articles by Taguchi, Zong Guofu, and Zhang Guanglei, "Testing on the Treatment of Raw Waste from High-Temperature Bacteria Isolated from Pandas", Biotechnology Journal, Vol. 79 No. 12, PP.463-469, 2001

<創作所欲解決之課題><Problems to be solved by creation>

然而,「堆肥型」型式的生垃圾處理機係一種將生垃圾發酵成為堆肥的方式,由於將裝置加熱至60℃附近來使用,因而有需要高的消耗電力及燃料費,以及花費高的運轉費用。又,在每次之生垃圾的處理中,必須取出堆肥,而且必須清理殘渣。又,由於高溫致使生垃圾發酵,導致會有臭氣的發生顯著、設置場所受到限制等之問題點。However, the "compost" type of garbage disposal machine is a method of fermenting garbage into compost. Since the device is heated to around 60°C and used, it requires high power consumption and fuel costs, and expensive operation. cost. In addition, in each treatment of raw garbage, compost must be taken out, and the residue must be cleaned up. In addition, due to the fermentation of raw garbage due to high temperature, there are problems such as the occurrence of significant odor and the limitation of the installation place.

又,在以往的「消滅型」生垃圾處理機及生垃圾處理方法中,處理生垃圾之微生物的處理能力也是低的,且不能夠以短時間來處理生垃圾。又,即使是假定能夠以短時進行生垃圾處理,在生垃圾分解的過程中,也會發生:生垃圾阻塞篩網、攪拌葉片之破損及固相處理槽浸沒於水中等之困擾,以致不能夠安定地持續使用。在專利文獻2中,雖然是記載了一種附設有發泡機構的裝置;雖然也有如專利文獻3所示之將攪拌翼加以變形而成者等,然而由於裝置的機構變複雜、攪拌葉片的構造變複雜,因而當金屬湯匙等之異物混入時,將會發生攪拌葉片與異物一起刮傷篩網、致使篩網破損之困擾。In addition, in the conventional "extinction type" garbage disposal machine and garbage disposal method, the treatment capacity of microorganisms for disposing of garbage is also low, and it is not possible to dispose of garbage in a short time. In addition, even if it is assumed that the garbage can be processed in a short time, during the decomposition of the garbage, it will also occur: the garbage blocks the screen, the stirring blade is damaged, and the solid-phase treatment tank is submerged in water, etc., so that it does not Able to continue to use stably. Patent Document 2 describes a device with a foaming mechanism attached; although there are also those that deform the stirring blade as shown in Patent Document 3, the structure of the device is complicated, and the structure of the stirring blade It becomes complicated, so when foreign substances such as metal spoons are mixed in, the stirring blade and the foreign substances will scratch the screen and cause the screen to be damaged.

本創作係為了解決如以上所述的課題而完成者,目的係在於提供一種用以長期且安定地使用之消滅型生垃圾機的處理方法。本創作中所稱之「生垃圾」,有時亦稱為廚餘、食物垃圾、日常飲食廢棄物、或有機廢棄物。 <用以解決課題的手段> This creation was completed in order to solve the above-mentioned problems, and the object is to provide a disposal method of an eradicating garbage generator for long-term and stable use. The "raw garbage" in this creation is sometimes called food waste, food waste, daily food waste, or organic waste. <means to solve the problem>

為了解決上述課題,本創作之特徵是在於:該生垃圾處理方法中之生垃圾分解微生物為含有以寄存號碼:NITE P-02373所寄存的IMI-1(bacillus subtilis)、以寄存號碼:NITE P-02374所寄存的IMI-2(bacillus amyloliquefaciens)、或以寄存號碼:NITE P-023745所寄存的IMI-3(bacillus subtilis subsp. linaquosorum)中之至少一種,並與生垃圾混合在一起。In order to solve the above-mentioned problems, the characteristic of this creation is that the raw waste decomposition microorganisms in the raw waste treatment method include IMI-1 (bacillus subtilis) deposited with the deposit number: NITE P-02373, and the deposit number: NITE P -At least one of IMI-2 (bacillus amyloliquefaciens) deposited by 02374, or IMI-3 (bacillus subtilis subsp. linaquosorum) deposited by NITE P-023745, and mixed with raw garbage.

再者,另一特徴係在於:將該3種類之微生物中之2種類或3種類混合使用來做為分解生垃圾之微生物。In addition, another special feature lies in that two or three kinds of the three kinds of microorganisms are mixed and used as a microorganism that decomposes raw garbage.

又,再一特徵係在於:將在多孔質狀陶瓷和樹脂製的緩衝材上擔持有生垃圾分解微生物之微生物擔體、與生垃圾加以混合。Still another feature is that a microbial carrier that supports microorganisms for decomposing microorganisms on a porous ceramic and a buffer material made of resin is mixed with the garbage.

此外,還一特徵係在於:將多孔質狀陶瓷的形狀形成為直徑7mm~直徑10mm的球形;將樹脂製的緩衝材的形狀形成為內徑10mm、長度10mm~12mm的圓筒形。In addition, another feature is that the shape of the porous ceramic is formed into a spherical shape with a diameter of 7 mm to 10 mm, and the shape of the resin-made cushioning material is formed into a cylindrical shape with an inner diameter of 10 mm and a length of 10 mm to 12 mm.

另外,又一特徵係在於:在一具備有可裝入生垃圾而加以處理的固相處理槽、及持有用以攪拌生垃圾之攪拌葉片的攪拌手段之生垃圾處理裝置中,構成為在前述固相處理槽的底部中具有孔洞徑為1.5mm~2.0mm的篩網;前述攪拌葉片的前端與前述篩網間之間隔為10mm~30mm;在前述攪拌葉片的前端設置有橡膠部,在述攪拌葉片的動作時前述橡膠部為與前述篩網接觸。 <創作的效果> In addition, another feature is that in a raw garbage treatment apparatus provided with a solid-phase treatment tank that can be loaded with raw garbage and treated, and a stirring means holding a stirring blade for stirring raw garbage, the The bottom of the solid-phase treatment tank has a mesh with a hole diameter of 1.5 mm to 2.0 mm; the distance between the front end of the stirring blade and the screen is 10 mm to 30 mm; a rubber portion is provided at the front end of the stirring blade. During the operation of the stirring blade, the rubber portion is in contact with the screen. <Creation effect>

如以上所述,根據本創作,提案一種摻混有上述的3種類之微生物之生物製劑,藉由以多孔質狀的球狀陶瓷(擔體A)及圓筒形(內徑φ10mm×長度10~12mm)的樹脂製的擔體B做為緩衝材來使用,能夠以短時間、安全且確實地分解生垃圾之生垃圾的處理方法。As mentioned above, according to this creation, a biological preparation blended with the above three types of microorganisms is proposed by using a porous spherical ceramic (support A) and a cylindrical shape (inner diameter φ10mm×length 10) ~12mm) The resin-made support B is used as a cushioning material, and can dispose of raw garbage in a short time, safely and reliably.

另外,多孔質狀的球狀陶瓷係在其表面與多孔質部具有使微生物增殖的效果、並且具有可以其自重而將生垃圾壓碎減小、將難以分解的纖維質加以切分破斷的效果。圓筒形的樹脂製擔體B係具有分散在裝置底面部中之因多孔質狀的球狀陶瓷的壓力所引起之裝置的摩耗之效果,並且在圓筒形的表裏面的凹凸成為微生物的擔體。又,同時地,藉由圓筒形的空間來確保在生垃圾中之空間,並成為分解生垃圾所需要的氧供給方,並且當圓筒形的樹脂製擔體B與多孔質狀的球狀陶瓷(擔體A)一起投入生垃圾處理時,也持有縮短生垃圾的分解時間之效果。In addition, the porous spherical ceramic system has the effect of multiplying microorganisms on the surface and the porous part, and has the ability to crush the raw garbage by its own weight, and cut the fiber that is difficult to decompose. effect. The cylindrical resin support B has the effect of wear of the device due to the pressure of the porous spherical ceramic dispersed in the bottom of the device, and the irregularities on the surface of the cylindrical surface become microorganisms Carrying body. Also, at the same time, the space in the raw garbage is ensured by the cylindrical space, and becomes the oxygen supplier required to decompose the raw garbage, and when the cylindrical resin support B and the porous ball When the shaped ceramics (loaded body A) are put into the disposal of raw garbage, it also has the effect of shortening the decomposition time of the raw garbage.

又,提案一種生垃圾的處理方法,其係藉由使用一種將在固相處理槽的底部之篩網的孔洞徑設為1.5mm~直徑2.0mm、將攪拌葉片間之間隔設為10mm~30mm、在攪拌葉片的前端附設有橡膠的葉片之構造,因而沒有裝置的破損及困擾,因而可長期且安定地進行生垃圾的處理。藉由將攪拌葉片的前端與固相處理槽的底部篩網間之間隔形成為10mm~30mm,能夠確保充分的淨空(clearance),即使是混入金屬湯匙等之異物,也能夠防止攪拌葉片與異物一起刮傷篩網、致使篩網破損之困擾。In addition, a method for treating raw garbage is proposed by using a method in which the hole diameter of the screen at the bottom of the solid-phase treatment tank is 1.5 mm to 2.0 mm in diameter, and the interval between the stirring blades is 10 mm to 30 mm. 1. The structure of the rubber blade is attached to the front end of the stirring blade, so there is no damage and trouble of the device, so the raw garbage can be disposed of for a long time and safely. By forming the gap between the front end of the stirring blade and the bottom screen of the solid-phase treatment tank to 10 mm to 30 mm, sufficient clearance can be ensured, even if foreign substances such as metal spoons are mixed in, the stirring blade and foreign substances can be prevented The problem of scratching the screen together and causing the screen to break.

但是,當將攪拌葉片的前端與固相處理槽的底部篩網間之間隔開設為10mm~30mm時,就不能夠攪拌在固相處理槽的底部附近的生垃圾,因而會有發生:處理生垃圾的能力降低及生垃圾阻塞篩網、固相處理槽浸沒於水中等之困擾。 因此,藉由在攪拌葉片的前端設置橡膠部,並固定與底部篩網部接觸之長度,所以即使是混入金屬湯匙等之異物,藉由橡膠的彈性效果也能夠防止固相處理槽的篩網刮傷破損之類的困擾。 However, when the distance between the front end of the stirring blade and the bottom screen of the solid-phase processing tank is set to 10 mm to 30 mm, it is impossible to stir the raw garbage near the bottom of the solid-phase processing tank, so there will be: The capacity of garbage is reduced and raw garbage blocks the screen, and the solid-phase treatment tank is submerged in water. Therefore, by providing a rubber part at the tip of the stirring blade and fixing the length in contact with the bottom screen part, even if foreign substances such as metal spoons are mixed, the elastic effect of the rubber can prevent the screen of the solid-phase treatment tank Troubles like scratches and damage.

又,由於攪拌葉片的旋轉時橡膠部絕對接觸於固相處理槽底部篩網部,所以能夠事前地防止因生垃圾所引起之篩網的阻塞。如此,藉由攪拌葉片的最適設計與前端部之橡膠的效果,因而能夠長期間沒有困擾續地使用生垃圾處理機。橡膠部的長度為自攪拌葉片的軸方向起向著篩網板之長度設為8cm~10cm,寬度設為9cm~11cm(處理能力為250kg/日的裝置)、19cm(處理能力為5 00kg/日的裝置)時,寬度係依裝置的容量比例放大。裝設成厚度為1cm~ 1.5cm(250處理能力為250kg/日的裝置)的長方形的形狀。In addition, since the rubber part is in absolute contact with the mesh part at the bottom of the solid-phase treatment tank when the stirring blade rotates, it is possible to prevent clogging of the mesh caused by raw garbage in advance. In this way, the optimal design of the stirring blade and the effect of the rubber at the front end make it possible to continue to use the garbage disposal machine for a long time without trouble. The length of the rubber part is 8cm to 10cm from the axial direction of the stirring blade to the screen plate, and the width is 9cm to 11cm (device with a processing capacity of 250kg/day), 19cm (processing capacity is 5000kg/day Device), the width is enlarged in proportion to the capacity of the device. It is installed in a rectangular shape with a thickness of 1 cm to 1.5 cm (apparatus with 250 processing capacity of 250 kg/day).

又,在本創作中所使用的微生物為一種中溫性微生物,由於最適使用溫度為15℃~35℃,所以就不需要如在堆肥型、及到現今為止的消滅型生垃圾處理機中所使用之好氣性微生物或高溫性微生物那樣地進行加溫,就能夠進行生垃圾之分解處理,所以裝置的製作費及維持費就便宜了。In addition, the microorganism used in this creation is a medium-temperature microorganism. Since the optimal use temperature is 15°C to 35°C, it does not need to be used in compost-type and the current eradication-type garbage disposal machines. By heating the used aerobic microorganisms or high-temperature microorganisms, the decomposition of raw garbage can be carried out, so the production and maintenance costs of the device are cheap.

根據本創作的生垃圾處理裝置,在標準條件中,與米飯或麵食類的處理時間為2小時至5小時、蔬菜或水果的處理時間為8小時至24小時之堆肥型、及現今的消滅型生垃圾處理機相比之下,使用本創作的微生物之生垃圾的處理時間能夠飛躍地以短時間進行處理。雖然會有處理纖維質多之洋蔥皮、及竹筍的皮等需要花費20小時以上的情況,然而只要是人類所能夠食用的食物,幾乎是皆能夠分解的。According to the raw garbage treatment device of this creation, under standard conditions, the processing time with rice or pasta is 2 hours to 5 hours, the processing time with vegetables or fruits is 8 hours to 24 hours, the compost type, and the current extinction type In comparison with the garbage disposal machine, the disposal time of the garbage produced using the microorganism of the present invention can be rapidly processed in a short time. Although it may take more than 20 hours to process the onion skin with a lot of fiber and bamboo skin, etc., as long as it is a food that can be eaten by humans, almost all can be decomposed.

在定期運轉中,採取本創作之生垃圾處理裝置的排水並加以計量時,氫離子濃度之數値為5.8(25℃)、生化需氧量(BOD)之數值為510mg/L。該數値是家庭排水中之1杯的味噌湯汁35000g/L、米的洗米水3000g/L,所以推測幾乎生垃圾皆被消除的程度。 如以上所述,可以確認:經由使用本創作的微生物之本創作的生垃圾處理方法,能夠飛躍地以短時間來處理生垃圾。 In the regular operation, when the drainage of the raw garbage treatment device of this creation is taken and measured, the value of hydrogen ion concentration is 5.8 (25°C), and the value of biochemical oxygen demand (BOD) is 510 mg/L. This value is 35,000g/L of miso soup in a cup of household drainage and 3000g/L of rice washing water, so it is estimated that almost all raw garbage is eliminated. As described above, it can be confirmed that the original garbage disposal method using microorganisms created by the author can rapidly process raw garbage in a short time.

以下,使用圖面來說明本創作之一實施例的形態。圖1係基於本創作之生垃圾處理方法的構成之斷面圖。圖2係顯示在圖1所例示之生垃圾處理方法的攪拌部之構成的一例子的部分圖。圖3係多孔質狀球狀陶瓷的外觀説明圖。圖4係圓筒形緩衝材的外觀説明圖。Hereinafter, the form of one embodiment of the present creation will be described using the drawings. Figure 1 is a cross-sectional view of the composition of the raw garbage treatment method based on this creation. FIG. 2 is a partial diagram showing an example of the configuration of the stirring section of the raw garbage treatment method illustrated in FIG. 1. Fig. 3 is a diagram illustrating the appearance of a porous spherical ceramic. Fig. 4 is an explanatory diagram of the appearance of a cylindrical buffer material.

例如,列舉說明裝置的一例,在圖1生垃圾處理機的固相處理槽底面部9中投入:寄存號碼:NITE P-02373所寄存的IMI-1(bacillus subtilis)、或寄存號碼:NITE P-02374所寄存的IMI-2(bacillus amyloliquefaciens) 、或寄存號碼:NITE P-02375所寄存的IMI-3(bacillus subtilis subsp. linaquosorum)中之任一者的分解生垃圾之微生物、或其組合而成的生物製劑,投入500g。在它之上,投入40kg之待處理的生垃圾。再於其上,投入20kg的多孔質陶瓷11 及125L的樹脂製的緩衝材12。該樹脂製緩衝材12,不限定是聚丙烯製,亦能夠使用聚乙烯、聚苯乙烯、聚氯化乙烯、聚乙烯、ABS樹脂及PET。For example, to give an example of an explanation device, put in the bottom part 9 of the solid-phase treatment tank of the garbage disposal machine of FIG. 1: deposit number: NITE P-02373 deposited IMI-1 (bacillus subtilis), or deposit number: NITE P -02374 deposited IMI-2 (bacillus amyloliquefaciens), or deposit number: NITE P-02375 deposited IMI-3 (bacillus subtilis subsp. linaquosorum) any one of the microorganisms that decompose raw garbage, or a combination thereof 500g of the prepared biological agent. On top of it, put 40kg of raw garbage to be treated. Furthermore, 20 kg of porous ceramics 11 and 125 L of resin-made cushioning material 12 were put on it. The resin-made buffer material 12 is not limited to polypropylene, and polyethylene, polystyrene, polyvinyl chloride, polyethylene, ABS resin, and PET can also be used.

在生垃圾中加入微生物的方法,雖然是沒有特別限定;然而,實用上是以擔持有上述微生物之著床擔體來形成微生物製劑,則就容易在它之中加入生垃圾。此時,也可以是將上述3種類之微生物混合使用,也可以是2種類的組合;或者也能夠使用1種類。由於是以中溫性微生物來做為生物製劑使用,處理生垃圾之溫度較佳為15℃至35℃,在超過35℃的情況下,由於微生物死亡活動遲緩,因而不是理想的。也不需要如一般的好氣性微生物高溫性微生物的那樣地使溫度上昇到37℃至65℃,所以能夠節省生垃圾處理裝置作動時的電氣費用、並且能夠減少裝置製造成本。Although the method of adding microorganisms to raw garbage is not particularly limited; however, in practice, it is easy to add raw garbage to it by forming a microbial preparation by supporting a carrier that supports the above microorganisms. In this case, the above three types of microorganisms may be used in combination, or a combination of two types may be used; or one type may be used. Due to the use of mesophilic microorganisms as biological agents, the temperature of raw garbage treatment is preferably 15°C to 35°C. When the temperature exceeds 35°C, the activity of microorganisms is slow, which is not ideal. There is no need to raise the temperature to 37°C to 65°C as with ordinary aerobic microorganisms and high-temperature microorganisms. Therefore, it is possible to save electrical costs when the garbage disposal device operates, and to reduce the device manufacturing cost.

投入生垃圾中之微生物量係依照生垃圾的組成、溫度空氣間之接觸程度等而變化。又,微生物本身由於是一邊分解生垃圾一邊繁殖,所以不能一律限定,然而,一般而言,對於100kg/日的生垃圾 (含有水分),生物製劑為750g、多孔質陶瓷11為30kg、樹脂製緩衝材12的容量為250Ⅼ。該標準條件中之生垃圾的處理時間,米飯或麵食類為花費2小時至5小時;蔬菜或水果為花費8小時至24小時。又,纖維質多的蔥的皮及竹筍的皮等也有花費20小時以上的情況。這是因為:在投入生垃圾處理機之前,由於事先細小化,所以能夠縮短處理時間。又,由於不能夠分解牛或豬等之大的骨頭,所以有必要事前先去除之。The amount of microorganisms put into the raw garbage varies according to the composition of the raw garbage and the degree of contact between the temperature and the air. In addition, the microorganism itself can not be limited because it proliferates while decomposing raw garbage. However, in general, for 100 kg/day of raw garbage (containing water), the biological preparation is 750 g, the porous ceramic 11 is 30 kg, and is made of resin. The capacity of the buffer material 12 is 250Ⅼ. The processing time of raw garbage in this standard condition is rice or pasta for 2 hours to 5 hours; for vegetables or fruits it takes 8 to 24 hours. In addition, the skin of onion and bamboo shoots with a lot of fiber may take more than 20 hours. This is because, before being put into the garbage disposal machine, the processing time can be shortened due to the miniaturization in advance. Also, since it is not possible to break down large bones such as cows or pigs, it is necessary to remove them beforehand.

生物製劑所含之微生物的大小是寬度為0.7~0.8μm、長度為2~3μm,在1g的生物製劑中生長著約2億個微生物。此等之微生物係經由攪拌葉片1的攪拌(標準條件為3RPM)而與多孔質陶瓷11及樹脂製緩衝材12混合在一起,然後,經由散水(標準條件為1小時3次,各1分鐘)而增殖。在理想的狀態下增殖的情況下,在1小時後增殖為約4倍的8億個,在24小時後增殖為1.7×10 18個。微生物係生長在多孔質陶瓷11的表面之多數個孔穴及樹脂製緩衝材12的表面積的空間部並增殖,經由攪拌而從其中飛散出來並開始分解生垃圾。即使是只以多孔質狀的球狀陶瓷擔體A,亦能夠使微生物增殖,當不加入圓筒形的聚丙烯製的擔體B時,則球狀陶瓷擔體A停留在生垃圾處理裝置固定處理槽底面部9,恐怕會致使裝置底面部磨耗。藉由加入圓筒形的聚丙烯製的擔體B時,則微生物會在圓筒形的表裏面增殖,並且擔任分散裝置底面部中之壓力的角色。多孔質狀的球狀陶瓷擔體A,當球徑成為φ4mm以下時,則就會產生浮力而懸浮於水中,以致切分破斷生垃圾的效果下降,因而有必要定期補充。做為生物製劑使用的微生物也就不會永久持續地增殖,3週~4週的壽命而死亡、與排水一起被排出;或者有時也會因來自生垃圾所產生的雜菌而死亡等,因而有必要定期補充。 <實施例> The size of the microorganisms contained in the biological preparation is 0.7 to 0.8 μm in width and 2 to 3 μm in length, and about 200 million microorganisms grow in 1 g of the biological preparation. These microorganisms are mixed with the porous ceramic 11 and the resin-made buffer material 12 by stirring by the stirring blade 1 (standard condition is 3 RPM), and then passed through water (standard conditions are 1 hour and 3 times, 1 minute each) And proliferation. When multiplying in an ideal state, 800 million cells will multiply approximately 4 times after 1 hour, and 1.7×10 18 cells will multiply after 24 hours. Microorganisms grow in many holes on the surface of the porous ceramic 11 and in the space portion of the surface area of the resin-made buffer material 12 and multiply, and fly out of them by stirring and start to decompose raw garbage. Even if it is only a porous spherical ceramic support A, microorganisms can be multiplied. When the cylindrical polypropylene support B is not added, the spherical ceramic support A stays in the garbage disposal device Fixing the bottom part 9 of the treatment tank may cause wear on the bottom part of the device. When the cylindrical polypropylene-made support B is added, microorganisms will multiply in the cylindrical surface and act as the pressure in the bottom surface of the dispersing device. The porous spherical ceramic support A has a buoyancy and is suspended in water when the ball diameter is 4 mm or less, so that the effect of cutting and breaking raw garbage is reduced, so it is necessary to replenish regularly. Microorganisms used as biological agents will not proliferate permanently and will die for 3 to 4 weeks of life, and will be discharged together with drainage; or sometimes they will die due to contaminants from raw garbage. It is therefore necessary to supplement regularly. <Example>

為了檢驗基於微生物之生垃圾的分解效果,則使用寄存號碼:NITE P-02373所寄存的IMI-1(bacillus subtilis)、寄存號碼:NITE P-02374所寄存的IMI-2(bacillus amyloliquefaciens) 、寄存號碼:NITE P-02375所寄存的IMI-3 (bacillus subtilis subsp.linaquosorum)而分別地確認個別的微生物所持有之生垃圾處理能力。首先,在100ml的燒瓶中添加12g的生垃圾固形物及40ml的純水。在其中,加入0.5ml 的前述微生物經培養的液菌株IMI-1、IMI-2及IMI-3,於35℃振盪培養,以1.5 mm (孔) 篩分離固形物及懸浮物質。然後,以離心分離(10,000xg, 5 min, 4℃)來分離懸浮物質及上清液。然後,稀釋上清液,測定BOD (biochemical oxygen demand)或COD(chemical oxygen demand)。將實驗開始5日後的各燒瓶中之固形物及懸浮物質的重量表示於表-1中。 <表1>實驗開始5日後的各燒瓶中之固形物及懸浮物質的重量   固形物(g) 懸浮物質(g) 純水 1.9 11.6 IMI-1 0.2 6.2 IMI-2 0.2 11.8 IMI-3 0.2 6.4 與使用未添加培養微生物的純水之固形物量相比較之下,經添加培養IMI-1、IMI-2、及IMI-3 的固形物量約減少14.1%,而形成溶液化。可以推定是由於IMI-1、IMI-2、及IMI-3的添加效果,固形物被破壞變小,進而形成溶液化。可以推斷是因為與使用未添加培養IMI-1及IMI-3的純水之固形物與懸浮物質的總量相比之下,IMI-1及IMI-3的添加培養液之固形物及懸浮物質的總量減少約 47.4%及約 48.9%,經破壞的固形物形成溶液化、更進一步地成為有機物而被微生物所代謝。從以上的實驗結果來看,可以確認:IMI-1、IMI-2、及IMI-3對於生垃圾的溶液化是有效的事實;還可以確認:IMI-1及IMI-3 對於有機物(固形物、及懸浮物質)的代謝是有效的事實。 <產業可利用性> In order to test the decomposition effect of microorganism-based raw garbage, the deposit number: IMI-1 (bacillus subtilis) deposited by NITE P-02373, deposit number: IMI-2 (bacillus amyloliquefaciens) deposited by NITE P-02374, deposit Number: IMI-3 (bacillus subtilis subsp.linaquosorum) deposited in NITE P-02375 and confirm the raw garbage disposal capacity held by individual microorganisms. First, add 12g of solid solid waste and 40ml of pure water to a 100ml flask. To this, 0.5 ml of the cultured liquid strains IMI-1, IMI-2 and IMI-3 of the aforementioned microorganisms were added, cultured with shaking at 35°C, and solids and suspended matter were separated with a 1.5 mm (hole) sieve. Then, centrifugal separation (10,000xg, 5 min, 4°C) was used to separate the suspended material and supernatant. Then, the supernatant is diluted to measure BOD (biochemical oxygen demand) or COD (chemical oxygen demand). The weight of the solid matter and suspended matter in each flask 5 days after the start of the experiment is shown in Table-1. <Table 1> The weight of solids and suspended matter in each flask 5 days after the start of the experiment Solids (g) Suspended material (g) Pure water 1.9 11.6 IMI-1 0.2 6.2 IMI-2 0.2 11.8 IMI-3 0.2 6.4 Compared with the amount of solids using pure water without added cultured microorganisms, the amount of solids with added cultures IMI-1, IMI-2, and IMI-3 was reduced by about 14.1% to form a solution. It can be presumed that due to the effects of the addition of IMI-1, IMI-2, and IMI-3, the solids are destroyed and reduced, and then form a solution. It can be inferred that this is because the solids and suspended substances added to the culture medium of IMI-1 and IMI-3 were compared with the total amount of solids and suspended substances that were not added with pure water for the cultivation of IMI-1 and IMI-3. The total amount is reduced by about 47.4% and about 48.9%. The destroyed solids form a solution, and further become organic matter and are metabolized by microorganisms. From the above experimental results, it can be confirmed that: IMI-1, IMI-2, and IMI-3 are effective for the liquefaction of raw waste; it can also be confirmed that IMI-1 and IMI-3 are effective for organic matter (solid matter) , And suspended substances) is an effective fact. <Industry availability>

本創作係能夠利用在以房屋內部(in-house)及公共設施設處理生垃圾之提供法人使用的大型生垃圾處理機中之生垃圾的處理方法。This creative system can make use of the raw garbage disposal method in the large-scale raw garbage disposal machine provided by the legal person that uses the in-house and public facilities to deal with the raw garbage.

1、1a、1b、1c、1d‧‧‧攪拌葉片 2、2a、2b、2c、2d‧‧‧橡膠葉片 3‧‧‧軸 4‧‧‧篩網部 5‧‧‧裝置本體 6‧‧‧固相處理槽 7‧‧‧液相處理槽 8‧‧‧生垃圾投入口 9‧‧‧固相處理槽底面部 10、10a‧‧‧固定螺栓 11‧‧‧多孔質狀球狀陶瓷 12‧‧‧樹脂製緩衝材1, 1a, 1b, 1c, 1d ‧‧‧ stirring blade 2. 2a, 2b, 2c, 2d 3‧‧‧axis 4‧‧‧ Screen Division 5‧‧‧device body 6‧‧‧Solid treatment tank 7‧‧‧Liquid treatment tank 8‧‧‧ Raw waste input 9‧‧‧Solid phase treatment tank bottom face 10, 10a‧‧‧ fixing bolt 11‧‧‧Porous spherical ceramic 12‧‧‧Resin buffer

圖1係顯示基於本創作之生垃圾處理方法的構成之一例子的斷面圖。 圖2係顯示在圖1所例示之生垃圾處理方法的攪拌部之構成的一例子的部分圖。 圖3係基於本創作之多孔質狀球狀陶瓷的外觀圖。 圖4係基於本創作之圓筒形緩衝材的外觀圖。 FIG. 1 is a cross-sectional view showing an example of the composition of a method for processing raw garbage based on this creation. FIG. 2 is a partial diagram showing an example of the configuration of the stirring section of the raw garbage treatment method illustrated in FIG. 1. Figure 3 is the appearance of the porous spherical ceramic based on this creation. Figure 4 is an external view of the cylindrical cushioning material based on this creation.

1‧‧‧攪拌葉片 1‧‧‧ stirring blade

2‧‧‧橡膠葉片 2‧‧‧rubber blade

3‧‧‧軸 3‧‧‧axis

4‧‧‧篩網部 4‧‧‧ Screen Division

5‧‧‧裝置本體 5‧‧‧device body

6‧‧‧固相處理槽 6‧‧‧Solid treatment tank

7‧‧‧液相處理槽 7‧‧‧Liquid treatment tank

8‧‧‧生垃圾投入口 8‧‧‧ Raw waste input

9‧‧‧固相處理槽底面部 9‧‧‧Solid phase treatment tank bottom face

Claims (1)

一種生垃圾處理裝置,其特徵在於:具備有用於裝入生垃圾並加以處理的固相處理槽、及持有用於攪拌生垃圾的攪拌葉片之攪拌手段;該生垃圾處理裝置係構成為:在前述固相處理槽的底部具有孔洞徑為1.5 mm~2.0mm的篩網;前述攪拌葉片的前端與前述篩網之間隔為10mm~30mm;前述攪拌葉片的前端設置有橡膠部;在前述攪拌葉片作動時,前述橡膠部為和前述篩網接觸。A raw garbage treatment device is characterized by comprising a solid-phase treatment tank for loading and processing raw garbage, and a stirring means holding a stirring blade for stirring raw garbage; the raw garbage treatment device is configured as follows: The bottom of the solid-phase treatment tank has a mesh with a hole diameter of 1.5 mm to 2.0 mm; the distance between the front end of the stirring blade and the screen is 10 mm to 30 mm; the front end of the stirring blade is provided with a rubber portion; When the blade is actuated, the rubber part comes into contact with the screen.
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