JP6515627B2 - Method and apparatus for removing methane fermentation unsuitable - Google Patents
Method and apparatus for removing methane fermentation unsuitable Download PDFInfo
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- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 title claims description 84
- 238000000855 fermentation Methods 0.000 title claims description 41
- 230000004151 fermentation Effects 0.000 title claims description 41
- 238000000034 method Methods 0.000 title claims description 18
- 238000003756 stirring Methods 0.000 claims description 54
- 239000000126 substance Substances 0.000 claims description 25
- 239000010815 organic waste Substances 0.000 claims description 22
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 19
- 229910052791 calcium Inorganic materials 0.000 claims description 19
- 239000011575 calcium Substances 0.000 claims description 19
- 239000012535 impurity Substances 0.000 claims description 10
- 239000000463 material Substances 0.000 claims description 9
- 239000011368 organic material Substances 0.000 claims 1
- 210000003278 egg shell Anatomy 0.000 description 47
- 102000002322 Egg Proteins Human genes 0.000 description 29
- 108010000912 Egg Proteins Proteins 0.000 description 29
- 238000000926 separation method Methods 0.000 description 27
- 239000002002 slurry Substances 0.000 description 17
- 239000010813 municipal solid waste Substances 0.000 description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 9
- 230000005484 gravity Effects 0.000 description 8
- 239000010794 food waste Substances 0.000 description 5
- 238000009825 accumulation Methods 0.000 description 4
- 239000005416 organic matter Substances 0.000 description 4
- 239000000356 contaminant Substances 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- 238000012546 transfer Methods 0.000 description 3
- 241000208340 Araliaceae Species 0.000 description 2
- 240000007594 Oryza sativa Species 0.000 description 2
- 235000007164 Oryza sativa Nutrition 0.000 description 2
- 235000005035 Panax pseudoginseng ssp. pseudoginseng Nutrition 0.000 description 2
- 235000003140 Panax quinquefolius Nutrition 0.000 description 2
- 235000013339 cereals Nutrition 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 235000008434 ginseng Nutrition 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 235000009566 rice Nutrition 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 230000007928 solubilization Effects 0.000 description 2
- 238000005063 solubilization Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 230000000007 visual effect Effects 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 235000009508 confectionery Nutrition 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- -1 eggshell Chemical compound 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 235000021478 household food Nutrition 0.000 description 1
- 238000002955 isolation Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 238000005457 optimization Methods 0.000 description 1
- 229920000915 polyvinyl chloride Polymers 0.000 description 1
- 239000004800 polyvinyl chloride Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000001612 separation test Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 230000003381 solubilizing effect Effects 0.000 description 1
- 239000011550 stock solution Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
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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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
Description
本発明は、家庭系生ごみや料理店などの事業系生ごみから排出される、生ごみなどに含まれる卵殻等のメタン発酵不適物を除去する方法と装置に関するものである。 The present invention relates to a method and apparatus for removing methane fermentation unsuitable substances such as eggshells contained in food waste and the like discharged from household food waste and business food waste such as a restaurant.
家庭や料理店、菓子店などから排出される生ごみや食品製造工場、畜産場などから排出される生ごみを処理する方法のひとつとしてメタン発酵法がある。その場合、これらの生ごみに含まれている卵殻等の無機物はメタン発酵処理の対象外であるので、一般に、生ごみに水を加えてスラリーとし、これを長時間放置することにより卵殻等を沈降させて分離している。 There is a methane fermentation method as one of the methods to process the garbage discharged from homes, restaurants, confectionery stores and the like, and the food manufacturing factory and the fishery factory. In that case, since inorganic substances such as eggshells contained in these raw wastes are not subject to methane fermentation treatment, in general, water is added to raw wastes to form a slurry, which is left for a long time to keep eggshells etc. It is separated by settling.
例えば、特許文献1には、有機性廃棄物を分離槽内に投入して、有機物とカルシウム含有夾雑物の可溶化時間の差を利用して、有機物の可溶化を進行させ、未可溶化状態で残存したカルシウム含有夾雑物を比重差により分離し、沈殿したカルシウム含有夾雑物を分離槽の底部から排出する方法が記載されている。
For example, according to
しかしながら、生ごみ中の有機物を可溶化させてから卵殻等を沈降分離させる方法は、分離槽内の滞留時間が長く装置が非常に大型になる。また、スラリーの粘性が高くなると分離が不能になるという問題がある。特に、卵殻などの可溶性カルシウムは、一旦溶解したものが環境の変化等で析出して受入分別装置から調整槽への移送配管、発酵槽以降の配管、発酵残渣貯留槽、汚泥処理設備配管などの各所で配管の閉塞等のトラブルを引き起こしている。 However, in the method of solubilizing organic matter in food waste and then settling and separating eggshells and the like, the residence time in the separation tank is long and the apparatus becomes very large. In addition, there is a problem that separation becomes impossible when the viscosity of the slurry becomes high. In particular, soluble calcium, such as eggshell, which has been dissolved once precipitates due to changes in the environment, etc. Transfer piping from the receiving separation device to the adjustment tank, piping after the fermentation tank, fermentation residue storage tank, sludge treatment facility piping, etc. It causes troubles such as blockage of piping in various places.
本発明の目的は、卵殻等のメタン発酵不適物を含有する有機性廃棄物から、配管トラブル等を引き起こす卵殻等のメタン発酵不適物を安価で効率よく除去する方法と装置を提供することにある。 An object of the present invention is to provide a method and apparatus for efficiently removing methane fermentation unsuitable substances such as eggshells causing piping troubles and the like from organic wastes containing methane fermentation unsuitable substances such as eggshells at low cost. .
本発明者らは、上記課題を解決するべく鋭意検討の結果、従来の沈降分離方式から、装置内に縦方向の旋回流を発生させて、生ごみスラリーを流動させることで、比重の大きい卵殻等の発酵不適物を短時間に効率よく分離でき、しかも、この方法は適応可能なスラリー粘度の幅が非常に広いことを見出した。より具体的には、分離槽に攪拌羽根を2段に設けて旋回流を形成させ、この攪拌羽根の位置や径、さらには回転数を調整することによって卵殻等を効率よく沈降分離できる範囲があることを見出し、この攪拌槽とした分離槽の底部を逆錐状にすることによって底部中央に卵殻等を効率よく集めて分離できることを見出した。 As a result of intensive studies to solve the above problems, the inventors of the present invention have generated swirl flow in the longitudinal direction in the apparatus from the conventional sedimentation separation method to flow the garbage slurry, thereby achieving a large specific gravity eggshell. Etc. It has been found that it is possible to efficiently separate out the fermentation unsuitable substances in a short time, and furthermore, this method has a very wide range of applicable slurry viscosity. More specifically, a stirring vessel is provided in two stages in the separation tank to form a swirling flow, and by adjusting the position and diameter of the stirring fan, and further adjusting the number of rotations, the range in which eggshells etc. can be efficiently separated and separated is It has been found that it is possible to efficiently collect and separate eggshells and the like in the center of the bottom by making the bottom of the separation tank used as the stirring tank inverted.
すなわち、本発明は、
カルシウムを含有するメタン発酵不適物を含み、粘度が8Pa・s以下の有機性廃棄物を、下向き錐形状を有する底部と2段の攪拌羽根を備えた攪拌槽に送入し所定の回転数で攪拌することにより、前記有機性廃棄物に含まれる前記メタン発酵不適物を前記攪拌槽の底部に集積させ分離することを特徴とするカルシウムを含有するメタン発酵不適物の除去方法と、
上記のカルシウムを含有するメタン発酵不適物の除去方法において使用するメタン発酵不適物の除去装置であって、下向き錐形状の底部を有する、カルシウムを含有するメタン発酵不適物を含む有機性廃棄物の攪拌槽と、前記攪拌槽の内容物を攪拌する2段の攪拌羽根を備えた攪拌機と、前記攪拌槽の底部に集積した前記メタン発酵不適物の排出手段と、前記メタン発酵不適物が分離された有機性廃棄物の排出手段を備えたカルシウムを含有するメタン発酵不適物の除去装置と、
前記2段の攪拌羽根のうち、前記攪拌槽の底部の上端と下段の羽根との間隔と、下段の羽根と上段の羽根との間隔が略等しく、上段の羽根径が下段の羽根径よりも大きいことを特徴とする上記のカルシウムを含有するメタン発酵不適物の除去装置
を提供するものである。
That is, the present invention
An organic waste containing calcium-containing methane fermentation impurities and having a viscosity of 8 Pa · s or less is fed into a stirring vessel equipped with a bottom having a downward cone shape and a two-stage stirring blade, and at a predetermined rotation speed A method of removing a methane-containing unsuitable substance containing calcium, characterized in that the methane-fermented unsuitable material contained in the organic waste is accumulated and separated at the bottom of the stirring tank by stirring;
An apparatus for removing methane fermentation impurities which is used in the method for removing methane fermentation impurities comprising calcium described above, which is an organic waste containing calcium fermentation methane unsuitable substances having a bottom in the shape of a downward cone. A stirring vessel, a stirrer provided with a two-stage stirring blade for stirring the contents of the stirring vessel, a discharge means for the methane fermentation non-suitable substance accumulated at the bottom of the stirring vessel, and the methane fermentation non-suitable substance An apparatus for removing calcium-containing methane fermentation impurities having organic waste discharge means,
Among the two-stage stirring blades, the distance between the upper end and the lower blade of the bottom of the stirring tank and the distance between the lower blade and the upper blade are substantially equal, and the upper blade diameter is larger than the lower blade diameter. It is an object of the present invention to provide an apparatus for removing the above-mentioned calcium-containing methane fermentation material which is characterized by being large.
本発明によれば、卵殻等のメタン発酵不適物を含む有機性廃棄物から、このメタン発酵不適物を短時間に効率よく分離できる。本発明の方法と装置は、適応可能なスラリー粘性の幅が非常に広いので、搬入スラリー濃度、粘性の変動に対しての対応が可能である。 According to the present invention, the methane fermentation non-suitable substance can be efficiently separated from the organic waste containing the methane fermentation non-suitable substance such as eggshell in a short time. Since the method and apparatus of the present invention have a very wide range of applicable slurry viscosity, it is possible to cope with fluctuations in the input slurry concentration and viscosity.
本発明の処理対象である有機性廃棄物は、カルシウムを含有するメタン発酵不適物を含むものである。カルシウムを含有するメタン発酵不適物とは、卵殻、貝殻等であり、比重は2.40〜3.00g/mL程度、通常2.60〜2.84g/mL程度のものである。これらを含む有機性廃棄物とは、例示すれば、家庭から排出される生活ごみ、料理店あるいはその他の飲食店から排出される生ごみ、スーパーやコンビニから排出される生ごみ等である。この有機性廃棄物に水を加えてスラリー化する。本発明の方法は、スラリー粘度については、幅広く、8Pa・s以下のものに対して適応できる。8Pa・sを越えると、メタン発酵不適物の分離効率が低下する。好ましい粘度は0.1〜8.0Pa・sの範囲であり、特に好ましい粘度は0.4〜5.0Pa・sの範囲である。また、スラリー状態の比重はほぼ1g/mLであり、通常1.00〜1.05g/mL程度である。 The organic wastes to be treated according to the present invention include calcium-containing methane fermentation unsuitable substances. The methane fermentation unsuitable substances containing calcium are eggshells, shells and the like, and the specific gravity is about 2.40 to 3.00 g / mL, usually about 2.60 to 2.84 g / mL. The organic wastes including these are, for example, household waste discharged from a home, raw garbage discharged from a restaurant or other restaurant, raw garbage discharged from a supermarket or a convenience store, and the like. Water is added to the organic waste to form a slurry. The method of the present invention is widely applicable to slurry viscosity of 8 Pa · s or less. When the pressure exceeds 8 Pa · s, the separation efficiency of methane fermentation unsuited substances decreases. The preferred viscosity is in the range of 0.1 to 8.0 Pa · s, and the particularly preferred viscosity is in the range of 0.4 to 5.0 Pa · s. In addition, the specific gravity of the slurry state is about 1 g / mL, and usually about 1.00 to 1.05 g / mL.
このような有機性廃棄物を攪拌槽に投入する。有機性廃棄物は、予めスラリーにしておいてもよく、また、攪拌槽に投入後水を加えてスラリーにしてもよい。 Such organic waste is charged into a stirred tank. The organic waste may be previously made into a slurry, or water may be added after being introduced into a stirring tank to make a slurry.
この攪拌槽は底部が下向き錐形状をしている。底部を下向き錐形状にするのは、そこにメタン発酵不適物を集積させるためであり、錐面の角度は、攪拌槽の水平面(軸を直角の面)に対し30〜60度程度が適当である。この錐形状は、通常は円錐であるが角錐等であってもよい。 The bottom of the stirring tank is in the shape of a downward cone. The reason for making the bottom part in the shape of a downward cone is to accumulate methane fermentation unsuitable substances there, and the angle of the cone surface is suitably about 30 to 60 degrees with respect to the horizontal plane (the plane perpendicular to the axis) of the stirring tank is there. The cone shape is usually a cone but may be a pyramid or the like.
攪拌槽は内部に攪拌機を設けてスラリーの縦方向の旋回流を形成させ、スラリーを流動化する。旋回流は、槽の周面側を上向流あるいは下向流、従って、槽の中央部を下向流あるいは上向流のいずれでもよいが、周面側を下向流、中央部を上向流とすることが好ましい。この旋回流によって比重の大きいメタン発酵不適物を槽底部の中央に沈降集積させる。そのために、攪拌機の撹拌羽根を2段とする必要があることを本発明者らは見出した。攪拌羽根は、縦方向の旋回流を形成するために、プロペラ翼や翼面を斜めにしたパドル翼などが用いられる。いずれにしてもメタン発酵不適物を沈降集積させる条件は非常にデリケートであり、基本的には各攪拌槽ごとに試験をして設定するのがよいが、攪拌羽根の位置と径は重要である。具体的には、攪拌槽の底部の上端(下向き錐形状の上縁)と下段の羽根との間隔と、下段の羽根と上段の羽根との間隔を略等しく、上記2つの間隔の比を1:0.5〜2程度、好ましくは1:0.75〜1.5程度とし、さらに好ましくは1:0.8〜1.3程度、また、上段の羽根の径を下段の羽根の径より大きく、上段の羽根の径/下段の羽根の径を1.1〜2程度、好ましくは1.2〜1.5程度とするのがよい。 The stirring tank is provided with a stirrer inside to form a longitudinal swirling flow of the slurry to fluidize the slurry. The swirling flow may be upward or downward flow on the circumferential surface side of the tank, and thus may be either downward or upward flow at the central portion of the tank, but downward flow on the circumferential surface side and upward on the central portion It is preferable to make it countercurrent. By this swirling flow, methane fermentation unsuitables having a large specific gravity are deposited and accumulated at the center of the bottom of the tank. The inventors have found that it is necessary to provide two stages of stirring blades for the stirrer. As the stirring blade, a propeller blade, a paddle blade with an inclined blade surface, or the like is used to form a swirling flow in the longitudinal direction. In any case, the conditions for sedimentation and accumulation of methane fermentation unsuitable substances are very delicate, and basically it is preferable to set and test each stirring tank, but the position and diameter of the stirring blade are important . Specifically, the distance between the upper end of the bottom of the stirring vessel (the upper edge of the downward cone shape) and the blades of the lower stage and the distance between the lower blades and the upper blades are approximately equal, and the ratio of the above two intervals is 1 0.5 to 2, preferably 1: 1: 0.75 to 1.5, more preferably 1: 0.8 to 1.3, and the diameter of the upper blade is greater than the diameter of the lower blade The diameter of the upper blade / the diameter of the lower blade may be about 1.1 to 2, preferably about 1.2 to 1.5.
攪拌槽には、さらに、有機性廃棄物の投入口、底部に集積したメタン発酵不適物の排出口およびメタン発酵不適物が分離された有機性廃棄物の排出口が設けられる。 The stirring tank is further provided with an inlet for organic waste, an outlet for methane fermentation nonconforming material accumulated at the bottom, and an outlet for organic waste from which the methane fermentation nonconforming material is separated.
メタン発酵不適物を攪拌槽の底部に集積させる条件として攪拌機の回転数も重要であり、スラリーの濃度や粘性等に応じて制御する必要がある。一方、攪拌時間は短時間でよく、攪拌槽の規模によるが1分〜1時間程度、通常2分〜15分程度でよい。また、メタン発酵不適物は100%除去する必要はなく、実用上、除去率は70〜
95%程度でよい。
The rotation speed of the stirrer is also important as a condition for accumulating the methane fermentation unsuitable substance on the bottom of the stirring tank, and it is necessary to control according to the concentration, viscosity, etc. of the slurry. On the other hand, the stirring time may be short, and may be about 1 minute to 1 hour, usually about 2 minutes to 15 minutes, depending on the size of the stirring tank. In addition, it is not necessary to remove 100% of methane fermentation unsuitable substances, and the removal rate is practically 70
It should be about 95%.
メタン発酵不適物を除去した有機性廃棄物は、メタン発酵させてメタンガスを製造することができる。一方、卵殻、貝殻等のメタン発酵不適物は、洗浄して、チョークやその他の用途に有効利用することができる。 The organic waste from which methane fermentation impurities are removed can be methane fermented to produce methane gas. On the other hand, methane fermentation unsuitable substances such as eggshells and shells can be washed and used effectively for chalk and other applications.
図1に示す装置を用いた。この装置は、攪拌槽1が内径が200mm、高さが300mm、の円筒形で、底部2が水平面に対する角度が30度の下向き円錐状をしており、底部2からは、この円筒が下に脚部3として100mm延設されている。本体1の側壁には、底部2から上180mmのところに有機性廃棄物投入口4が、底部2のやや上には卵殻を除去した卵殻分離液の排出口5が、そして底部2の中心には卵殻濃縮液の排出口6が設けられ、それぞれに弁を有する配管が接続されている。攪拌槽の容積は約9Lであり、材質はいずれも透明のポリ塩化ビニルでできている。攪拌槽1の中央には攪拌機7が軸を垂直にして設置され、軸の下端とそのやや上に攪拌羽根8が取着されている。この攪拌羽根は上下いずれも角度を45度にした6枚のパドル翼よりなり、羽根径(Φ)は80mm、100mm、120mmの3種類が準備されている。
The apparatus shown in FIG. 1 was used. In this apparatus, the
この装置を用い、まず、粘度0.85〜1.35Pa・s、密度約1.0g/mL、TS(蒸発残留物)3.6〜5.1重量%、卵殻濃度0.7〜3.6g・dry卵殻/kg・wet原料の家庭系生ごみについて、攪拌羽根の段数、羽根の径、下段の羽根の底部からの高さ、および羽根の間隔を変えて卵殻の分離試験を行った。 Using this apparatus, first, a viscosity of 0.85 to 1.35 Pa · s, a density of about 1.0 g / mL, a TS (evaporation residue) of 3.6 to 5.1% by weight, and an eggshell concentration of 0.7 to 3. Eggshell separation tests were conducted on 6-g · dry eggshell / kg · wet raw household garbage by changing the number of stages of stirring blades, the diameter of the blades, the height from the bottom of the lower blade, and the distance between the blades.
卵殻濃度の分析方法は、以下の方法で行った。
(1)原液、濃縮液、分離液の各サンプルを十分に混合して約200mL採取し、500mLビーカーに移す。(採取量を記録する。)
(2)金属性バット内に上記ビーカーを移し、攪拌機によって穏やかに攪拌する。
(3)ビーカー内に穏やかに流水を投入し、比重の小さい有機物やポリマー等を流水とともにビーカーから排出する。
(4)ビーカーから排出される水が透明になった時点で流水を停止する。
(5)ビーカー内の残液(比重の大きい固形物や一部のポリマーが残存)を篩(1mm、2.8mm、4mm)に流す。2〜3回ビーカーに水を入れて、内容物を充分に篩に移す。
(6)篩に水を流し、篩(メッシュ)に捕捉された固形物を篩上に広げる。
(7)篩にある卵殻をピンセットで採取し、事前に重量を測定したアルミカップにいれる。
(8)110℃で1晩乾燥し、重量を測定する。
(9)次の計算式から卵殻量を求める。
結果を表1に示した。条件1〜3では、攪拌が不足したため、卵殻以外の有機物(人参、米粒等)が卵殻と同時に堆積し、卵殻を選択分離できなかった。また、条件7〜9では、攪拌が過剰であったため、底部に一度沈降した卵殻が攪拌流により巻き上げられ、卵殻除去量が低下する現象が観察された。条件4〜6において、卵殻を効率的に底部に集積させることができた。目視での比較では、条件4での卵殻分離状況が条件5、6での分離状況より多くの卵殻を選択的に集積していたため、条件4での検討を進めることとした。
The analysis method of eggshell concentration was performed by the following method.
(1) Each sample of the stock solution, the concentrated solution, and the separated solution is thoroughly mixed, collected to about 200 mL, and transferred to a 500 mL beaker. (Record the amount collected.)
(2) Transfer the beaker into a metal vat and gently stir with a stirrer.
(3) Gently pour running water into the beaker, and discharge organic substances, polymers and the like with small specific gravity from the beaker with running water.
(4) Stop running water when the water discharged from the beaker becomes clear.
(5) Pour the residual liquid (solids with a large specific gravity and a part of the polymer) in the beaker through a sieve (1 mm, 2.8 mm, 4 mm). Pour water into the beaker 2-3 times and transfer the contents thoroughly to the sieve.
(6) Pour the water through the sieve and spread the solids trapped on the sieve (mesh) on the sieve.
(7) Collect eggshells from the sieve with tweezers and place in a pre-weighed aluminum cup.
(8) Dry at 110 ° C. overnight and measure the weight.
(9) Calculate the eggshell quantity from the following formula.
The results are shown in Table 1. Under
次に、条件4での運転条件の最適化を検討した。実験での家庭系生ごみの性状は、粘性1.0〜1.35Pa・s、比重約1.0g/mL、TS4.9〜5.0重量%、卵殻濃度約3.5g・rdy卵殻/kg・wet原料であった。
1)分離時間の検討
回転数160rpmでの卵殻の集積状況を時間との関係について調べた。2分後と5分後で卵殻分離量はわずかに増加したが、ほとんど飽和していた。また、10分後の様子を観察しても、卵殻の集積状況は5分ごと同様であったため、分離時間は5分と非常に短時間で良いと考えられた。
2)回転数の検討
テスト装置諸元と分離時間を固定して、運転条件(回転数)による分離状況を調べた。140〜160rpmで最も分離効率が高くなった。また、140rpmより回転数が低い場合には、有機物(米粒や人参等)が卵殻と一緒に沈殿すること、160rpmより回転数が高い場合には、底部での攪拌流速が高く沈殿した卵殻が巻き上がることが確認された。
3)卵殻分離実験(生ごみの性状変動への対応方法)
家庭系生ごみ(粘度0.35〜8.0Pa・s、密度1g/mL、TS3.6〜5.1重量%、卵殻濃度0.7〜3.4g・dry卵殻/kg・wet原料)を用いて、テスト装置諸元と分離時間を固定して、卵殻分離状況を検証した。生ごみスラリーの粘度により、同じ回転数であっても、分離状況が異なることがわかった。そこで、生ごみスラリーの粘度と沈降分離に適正であった回転数および卵殻分離効率を表2に示した。ここで、分離効率は次式により算出した。
Next, optimization of operating conditions under
1) Examination of separation time The accumulation situation of eggshells at a rotational speed of 160 rpm was investigated in relation to time. The eggshell separation increased slightly after 2 and 5 minutes, but was almost saturated. Moreover, even if the situation after 10 minutes was observed, it was considered that the separation time was as short as 5 minutes because the accumulation situation of eggshells was similar every 5 minutes.
2) Examination of rotational speed With the test device specification and separation time fixed, the separation situation by the operating conditions (rotational speed) was investigated. The separation efficiency was highest at 140 to 160 rpm. In addition, when the rotation speed is lower than 140 rpm, the organic matter (rice grains, ginseng etc.) precipitates together with the eggshell, and when the rotation speed is higher than 160 rpm, the stirring velocity at the bottom is high and the precipitated eggshell is wound It was confirmed to go up.
3) Eggshell separation experiment (method to cope with the characteristic change of garbage)
Household garbage (viscosity 0.35 to 8.0 Pa · s, density 1 g / mL, TS 3.6 to 5.1% by weight, egg shell concentration 0.7 to 3.4 g · dry egg shell / kg · wet raw material) Using the test device specifications and the separation time, eggshell separation was verified. It was found that the separation situation was different even at the same rotation speed depending on the viscosity of the garbage slurry. Therefore, Table 2 shows the viscosity of the garbage and the rotation speed and eggshell separation efficiency appropriate for settling and separation. Here, the separation efficiency was calculated by the following equation.
生ゴミスラリーの粘度と分離に最適であった回転数の関係を図2に示した。図2より,粘性と回転数には正の相関が得られることがわかった。 The relationship between the viscosity of the raw garbage slurry and the rotational speed that was optimum for separation is shown in FIG. From FIG. 2, it was found that a positive correlation was obtained between viscosity and rotational speed.
本発明は、家庭や飲食店等から排出される生ごみ等の有機性廃棄物から、カルシウムを含有するメタン発酵不適物を効率よく分離できるので、これらの有機性廃棄物をメタン発酵させる方法に幅広く利用できる。 Since the present invention can efficiently separate calcium-containing methane fermentation unsuitable substances from organic wastes such as garbage discharged from homes and restaurants etc., the method for methane-fermenting these organic wastes It can be used widely.
1 攪拌槽
2 底部
3 脚部
4 有機性廃棄物投入口
5 卵殻分離液の排出口
6 卵殻濃縮液の排出口
7 攪拌機
8 攪拌羽根
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