JP6617868B2 - Membrane separation methane fermentation equipment - Google Patents
Membrane separation methane fermentation equipment Download PDFInfo
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- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 title claims description 230
- 238000000855 fermentation Methods 0.000 title claims description 120
- 230000004151 fermentation Effects 0.000 title claims description 119
- 238000000926 separation method Methods 0.000 title claims description 72
- 239000012528 membrane Substances 0.000 title claims description 42
- 238000003756 stirring Methods 0.000 claims description 63
- 239000010815 organic waste Substances 0.000 claims description 23
- 239000000463 material Substances 0.000 claims description 19
- 239000011575 calcium Substances 0.000 claims description 18
- 229910052791 calcium Inorganic materials 0.000 claims description 18
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 17
- 238000007599 discharging Methods 0.000 claims description 5
- 210000003278 egg shell Anatomy 0.000 description 42
- 102000002322 Egg Proteins Human genes 0.000 description 32
- 108010000912 Egg Proteins Proteins 0.000 description 32
- 239000007788 liquid Substances 0.000 description 15
- 238000000034 method Methods 0.000 description 15
- 239000010802 sludge Substances 0.000 description 14
- 239000002002 slurry Substances 0.000 description 14
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 11
- 239000010813 municipal solid waste Substances 0.000 description 10
- 239000002994 raw material Substances 0.000 description 8
- 239000000126 substance Substances 0.000 description 8
- 230000005484 gravity Effects 0.000 description 7
- 239000010794 food waste Substances 0.000 description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 4
- 238000013019 agitation Methods 0.000 description 4
- 238000004062 sedimentation Methods 0.000 description 4
- 241000894006 Bacteria Species 0.000 description 3
- 238000011156 evaluation Methods 0.000 description 3
- 238000001471 micro-filtration Methods 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- 244000000626 Daucus carota Species 0.000 description 2
- 235000002767 Daucus carota Nutrition 0.000 description 2
- 240000007594 Oryza sativa Species 0.000 description 2
- 235000007164 Oryza sativa Nutrition 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 2
- 210000000988 bone and bone Anatomy 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 235000013339 cereals Nutrition 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000010791 domestic waste Substances 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000005192 partition Methods 0.000 description 2
- 229920000915 polyvinyl chloride Polymers 0.000 description 2
- 239000004800 polyvinyl chloride Substances 0.000 description 2
- 235000009566 rice Nutrition 0.000 description 2
- 238000001612 separation test Methods 0.000 description 2
- 229910000029 sodium carbonate Inorganic materials 0.000 description 2
- 230000000007 visual effect Effects 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 1
- 241000238424 Crustacea Species 0.000 description 1
- 241000251539 Vertebrata <Metazoa> Species 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 150000001669 calcium Chemical class 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 235000009508 confectionery Nutrition 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000012510 hollow fiber Substances 0.000 description 1
- 235000021478 household food Nutrition 0.000 description 1
- 239000010806 kitchen waste Substances 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 238000000108 ultra-filtration 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
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/20—Waste processing or separation
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- Treatment Of Sludge (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
- Processing Of Solid Wastes (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Description
本発明は、家庭系生ごみや食品製造工場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カルシウムを含有するメタン発酵不適物を除去する装置を備えた膜分離メタン発酵装置に関するものである。 The present invention relates to a membrane-separated methane equipped with a device for removing calcium-containing unsuitable methane fermentation materials such as eggshells contained in food waste, etc. discharged from household food waste and business food waste such as food manufacturing factories. The present invention relates to a fermentation apparatus.
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。メタン発酵法のなかでメタン発酵菌を含む汚泥を膜分離して処理水を取り出す膜分離メタン発酵法は、汚泥を高濃度化できるため、メタン発酵槽の小型化やガス発生量増加が可能である。しかし、生ごみからの膜分離メタン発酵法の場合には、卵殻や貝殻に由来するカルシウムスケールによる膜目詰まりや配管等へのスケール生成に伴う閉塞が知られており、特許文献1や2という方法が開発されている。 There is a methane fermentation method as one of methods for treating garbage discharged from homes, restaurants, confectionery stores, etc., and food waste from food manufacturing factories, livestock farms and the like. In the methane fermentation method, the membrane separation methane fermentation method that separates sludge containing methane-fermenting bacteria and removes treated water can increase the concentration of sludge. is there. However, in the case of membrane separation methane fermentation from raw garbage, clogging due to calcium clogging derived from eggshells and shells and clogging due to scale generation in pipes, etc. are known. A method has been developed.
特許文献1の方法は、膜分離槽を隔壁で仕切ってメタン発酵槽からの流入側を卵殻や貝殻等の沈降槽としてこれらを分離し、隔壁を越流した液を膜分離する方法である。
The method of
また、特許文献2の方法は、膜透過液に炭酸ソーダを加えてカルシウムを炭酸カルシウムとして析出させて除去し、このカルシウムを除去した液を濃度調整液としてメタン発酵槽に返送して希釈する方法である。
Moreover, the method of
特許文献1の方法は、卵殻や貝殻等の沈降に時間がかかるため沈降槽を大きなものにする必要があり、沈降が不十分な状態で膜分離槽に送ると膜へのカルシウムの析出による目詰まりや、配管へのスケール生成による閉塞の問題がある。
The method of
特許文献2の方法は、メタン発酵槽内のカルシウム濃度を低下させるために相当量の濃度調整液をメタン発酵槽に返送する必要があってメタン発酵槽が大型になり、また、カルシウムを除去するための炭酸ソーダの使用にコストがかかるという問題もある。
In the method of
本発明の目的は、卵殻等の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から、配管トラブル等を引き起こす卵殻等のカルシウムを含有するメタン発酵不適物を安価に効率よく除去できる膜分離メタン発酵装置を提供することにある。 The object of the present invention is to perform membrane separation that can efficiently and efficiently remove methane fermentation inadequate materials containing calcium such as eggshells that cause piping troubles, etc., from organic waste containing methane fermentation inadequate materials such as eggshells. It is to provide a methane fermentation apparatus.
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、生ごみ等の有機性廃棄物スラリーを流動させることで、比重の大きい卵殻等のカルシウムを含有するメタン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有機性廃棄物スラリーの粘度範囲が広いことを見出した。より具体的には、攪拌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メタン発酵不適物を効率よく沈降分離できる範囲があることを見出し、この攪拌分離槽の底部を逆錐状にすることによって底部中央にメタン発酵不適物を効率よく集めて分離できることを見出した。そして、この攪拌分離槽は、汚泥を高濃度化してメタン発酵を効率的に行わせる膜分離メタン発酵法に特に適することを見出して本発明を完成するに至った。 As a result of intensive studies to solve the above problems, the present inventors have generated a swirl flow in the vertical direction in the apparatus from the conventional sedimentation separation method to flow organic waste slurry such as garbage. Thus, it has been found that methane fermentation unsuitable substances containing calcium such as eggshell having a large specific gravity can be efficiently separated in a short time, and that this method has a wide viscosity range of adaptable organic waste slurry. More specifically, a stirring blade is provided in two stages in the stirring separation tank to form a swirling flow, and by adjusting the position and diameter of the stirring blade and the rotation speed, the methane fermentation inappropriate material is efficiently settled and separated. It has been found that there is a possible range, and it has been found that by making the bottom of this stirred separation tank into an inverted cone shape, it is possible to efficiently collect and separate methane fermentation unsuitables at the center of the bottom. And it discovered that this stirring separation tank was especially suitable for the membrane separation methane fermentation method which makes sludge highly concentrated and performs methane fermentation efficiently, and came to complete this invention.
すなわち、本発明は、
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が投入される攪拌分離槽と、前記攪拌分離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、前記攪拌分離槽の底部に集積した前記メタン発酵不適物を排出するための排出手段とを備えた除去装置を、メタン発酵槽の前段に有し、かつメタン発酵槽の後段に膜分離槽を有することを特徴とする膜分離メタン発酵装置と、
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発酵液が投入される攪拌分離槽と、前記攪拌分離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、前記攪拌分離槽の底部に集積した前記メタン発酵不適物を排出するための排出手段とを備えた除去装置を、メタン発酵槽の後段かつ膜分離槽の前段に有することを特徴とする膜分離メタン発酵装置と、
前記2段の攪拌羽根のうち、前記攪拌分離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膜分離メタン発酵装置
を提供するものである。
That is, the present invention
A stirrer having a bottom-conical bottom portion into which an organic waste containing calcium-inappropriate methane fermentation containing organic waste is charged, and a stirrer equipped with two stirrer blades for stirring the contents of the stir separation tank And a removing device for discharging the inappropriate methane fermentation material accumulated at the bottom of the stirred separation tank, and a membrane separation tank at the rear stage of the methane fermentation tank. A membrane separation methane fermentation apparatus characterized by comprising:
A stirring / separating tank into which a fermentation broth containing a methane fermentation inappropriate material containing calcium and having a bottom-conical bottom portion is charged; and a stirrer equipped with two-stage stirring blades for stirring the contents of the stirring / separating tank; Membrane-separated methane, comprising a removal device provided with a discharging means for discharging the inappropriate methane fermentation material accumulated at the bottom of the stirred separation tank, at a stage subsequent to the methane fermentation tank and before the membrane separation tank A fermentation apparatus;
Among the two-stage stirring blades, the distance between the upper end of the bottom of the stirring separation tank and the lower blade is substantially equal to the distance between the lower blade and the upper blade, and the upper blade diameter is smaller than the lower blade diameter. The membrane-separated methane fermentation apparatus is characterized by being large.
本発明によれば、卵殻等の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から、このメタン発酵不適物を短時間に効率よく分離して膜分離メタン発酵を円滑に行うことができる。さらに、カルシウムを含有するメタン発酵不適物の除去装置によって、幅広い粘度範囲の有機性廃棄物スラリーに対して適用可能であるため、処理対象である有機性廃棄物の性状が変動した場合であっても安定して効率よく膜分離メタン発酵を行うことが可能となる。 According to the present invention, it is possible to efficiently perform membrane-separated methane fermentation by efficiently separating methane fermentation unsuitable materials in a short time from organic waste containing methane fermentation unsuitable materials containing calcium such as eggshell. . Furthermore, since it can be applied to organic waste slurries with a wide viscosity range by a device for removing inappropriate methane fermentation containing calcium, it can be used when the properties of organic waste to be treated fluctuate. In addition, it is possible to carry out membrane separation methane fermentation stably and efficiently.
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、脊椎動物の骨、甲殻類の外骨等であり、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した有機性廃棄物スラリー(以下、単に「スラリー」と呼ぶことがある)を原料とする。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除去率が低下する。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 waste which is the treatment target of the present invention includes a methane fermentation inappropriate material containing calcium. Inappropriate methane fermentation containing calcium is eggshell, seashell, vertebrate bone, crustacean outer bone, etc. Specific gravity is about 2.40 to 3.00 g / mL, usually about 2.60 to 2.84 g / mL. . The organic waste containing these includes, for example, household waste discharged from homes, garbage discharged from restaurants or other restaurants, food waste discharged from supermarkets and convenience stores, and the like. An organic waste slurry (hereinafter simply referred to as “slurry”) obtained by adding water to this organic waste to form a slurry is used as a raw material. The method of the present invention has a wide range of slurry viscosities, and can be applied to those of 8 Pa · s or less. If it exceeds 8 Pa · s, the removal rate of methane fermentation unsuitables 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. The specific gravity in the slurry state is about 1 g / mL, and is usually about 1.00 to 1.05 g / mL.
発酵汚泥は、上記有機性廃棄物をメタン発酵して発生した汚泥であり、メタン発酵槽から排出されるものである。発酵汚泥はTSが1.5〜3.0質量%、通常2.0〜2.5質量%程度である。 Fermented sludge is sludge generated by methane fermentation of the organic waste, and is discharged from the methane fermentation tank. The fermented sludge has a TS of 1.5 to 3.0% by mass, usually about 2.0 to 2.5% by mass.
メタン発酵は公知の方法に従って行えばよい。メタン発酵槽は、メタン発酵が嫌気発酵であり、また、発酵で生成したメタンを有効利用するために密閉構造とする。形状は箱形や円筒形などでよい。内部には攪拌機は設けなくてもよいが、ドラフトチューブなどを設けてもよい。 Methane fermentation may be performed according to a known method. The methane fermentation tank has a sealed structure in order to effectively use methane produced by fermentation, in which methane fermentation is anaerobic fermentation. The shape may be a box shape or a cylindrical shape. A stirrer may not be provided inside, but a draft tube or the like may be provided.
メタン発酵槽でメタン発酵が行われて流出する発酵液には、メタン菌が大量に含まれているので、メタン菌を高濃度に維持して発酵を効率よく行わせるために、膜分離槽で処理水を分離して残った発酵汚泥を回収してメタン発酵槽に返送する。このメタン発酵槽に付設する膜分離槽は特開2001−170631号公報に開示されているものを利用できる。用いる膜は、精密濾過膜(MF膜)、限外濾過膜(UF膜)等を用いることができ、膜の形状は、平膜、中空糸膜等がある。膜の下には散気装置を設けて膜面の流速を高めるとともに発酵汚泥等の膜面への付着を防止する。散気装置に使用するガスは、窒素ガスや炭酸ガスなどを用いてもよいが、メタン発酵で発生するメタンを主成分とするバイオガスを利用するのがよい。 The fermentation broth that is run out of methane fermentation in the methane fermentation tank contains a large amount of methane bacteria, so in order to maintain the methane bacteria at a high concentration and perform fermentation efficiently, Separate the treated water and collect the remaining fermentation sludge and return it to the methane fermentation tank. The membrane separation tank attached to this methane fermentation tank can utilize what is disclosed by Unexamined-Japanese-Patent No. 2001-170631. As the membrane to be used, a microfiltration membrane (MF membrane), an ultrafiltration membrane (UF membrane) or the like can be used, and the shape of the membrane includes a flat membrane, a hollow fiber membrane and the like. An air diffuser is provided under the membrane to increase the flow velocity of the membrane surface and prevent adhesion of fermented sludge and the like to the membrane surface. Nitrogen gas, carbon dioxide gas, or the like may be used as the gas used in the air diffuser, but biogas mainly composed of methane generated by methane fermentation is preferably used.
本発明の装置では、メタン発酵の対象物でないばかりでなく、膜面に析出して、膜分離を阻害したり、配管等に析出して流れ等を阻害するカルシウムなどの発酵不適物を除去する。 In the apparatus of the present invention, not only the object of methane fermentation, but also deposits on the membrane surface to inhibit membrane separation, or remove unsuitable fermentation materials such as calcium that deposit on pipes and inhibit flow and the like. .
本発明のメタン発酵不適物の除去装置の攪拌分離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、攪拌分離槽の水平面(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 separation tank of the apparatus for removing inappropriate methane fermentation according to the present invention has a downward cone shape. The bottom part is shaped like a downward cone in order to accumulate methane fermentation inappropriate substances there, and the angle of the cone face is suitably about 30 to 60 degrees with respect to the horizontal plane (the plane perpendicular to the axis) of the stirring separation tank. It is. The cone shape is usually a cone, but may be a pyramid or the like.
攪拌分離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、攪拌分離槽の周面側を上向流あるいは下向流、攪拌分離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、基本的には各攪拌分離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、攪拌分離槽の底部の上端(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 agitation / separation tank is provided with an agitator inside to form a vertical swirling flow of the slurry to fluidize the slurry. The swirling flow may be either an upward flow or a downward flow on the peripheral surface side of the stirring separation tank, and a downward flow or an upward flow on the central portion of the stirring separation tank. Is preferably an upward flow. By this swirl flow, unsuitable methane fermentation having a large specific gravity is settled and accumulated at the center of the bottom of the tank. For this purpose, the present inventors have found that the stirring blades of the stirrer need to have two stages. As the stirring blade, a propeller blade, a paddle blade having an inclined blade surface, or the like is used to form a vertical swirling flow. In any case, the conditions for sedimentation and accumulation of methane fermentation unsuitable substances are very delicate. Basically, it is better to test and set for each stirring separation tank, but the position and diameter of the stirring blades are important. is there. Specifically, the distance between the upper end of the bottom of the stirring separation tank (upper edge of the downward cone) and the lower blade and the distance between the lower blade and the upper blade are substantially equal, and the ratio of the two intervals is 1 : About 0.5 to 2, preferably about 1: 0.75 to 1.5, more preferably about 1: 0.8 to 1.3, and the diameter of the upper blade is smaller than the diameter of the lower blade. The diameter of the upper blade / the lower blade should be about 1.1 to 2, preferably about 1.2 to 1.5.
攪拌分離槽には、さらに、有機性廃棄物または発酵液の投入口、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除去された有機性廃棄物または発酵液の排出口が設けられる。 The agitation / separation tank further has an inlet for organic waste or fermentation liquid, an outlet for inappropriate methane fermentation accumulated at the bottom, and an outlet for organic waste or fermentation liquid from which inappropriate methane fermentation has been removed. Provided.
メタン発酵不適物を攪拌分離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度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、攪拌分離槽の規模によるが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 number of rotations of the stirrer is also important as a condition for accumulating unsuitable methane fermentation substances at the bottom of the stirring separation tank, and it is necessary to control according to the concentration and viscosity of the slurry. On the other hand, the stirring time may be short, depending on the scale of the stirring and separation tank, but may be about 1 minute to 1 hour, usually about 2 minutes to 15 minutes. Moreover, it is not necessary to remove 100% of methane fermentation unsuitable substances, and practically, the removal rate may be about 70 to 95%.
メタン発酵不適物の除去装置は、膜分離槽の前に設ければよく、メタン発酵槽の前に設けてもよく、メタン発酵槽と膜分離槽の間に設けてもよい。メタン発酵槽の前に設けることで、メタン発酵槽までの配管やメタン発酵槽内等でのスケール生成が抑制される。メタン発酵槽と膜分離槽の間に設けることで、発酵汚泥の固形物滞留時間が25〜35日程度と長いため、スラリーと比較して粘度等の性状の変動が小さく、メタン発酵不適物の分離条件の変更頻度が低減できる。 The apparatus for removing unsuitable methane fermentation may be provided in front of the membrane separation tank, may be provided in front of the methane fermentation tank, or may be provided between the methane fermentation tank and the membrane separation tank. By providing it in front of the methane fermentation tank, scale generation in the piping to the methane fermentation tank, the methane fermentation tank, or the like is suppressed. By providing it between the methane fermentation tank and the membrane separation tank, the solid residence time of the fermented sludge is as long as about 25 to 35 days. The frequency of changing separation conditions can be reduced.
本発明の一実施態様を図1に示す。この装置は、メタン発酵槽の前段にメタン発酵不適物の除去装置が設けられている。生ごみ等の有機性廃棄物が攪拌分離槽に入れられる。攪拌分離槽内では生ごみ中の卵殻等のメタン発酵不適物が沈降して下端の排出口から連続的あるいは間欠的に排出される。メタン発酵不適物が除去された有機性廃棄物はメタン発酵槽に供給されてメタン発酵が行われ、メタン発酵槽からは発酵液が連続的あるいは間欠的に抜き出されて膜分離槽に送られる。膜分離槽で発酵液が処理水と発酵汚泥に分離される処理水は、SSやCODMn等の有機物濃度が低いため、下水道放流等の後処理が簡易になる。メタン発酵槽内で発生した、主にメタンと炭酸ガスからなるバイオガスは発電燃料等に利用できる。バイオガスの一部は送風機等を介して膜分離槽に送り、散気に利用される。生ごみ等は必要により水とともに直接メタン発酵槽に投入することもでき、あるいは調整槽を設けてそこで水を加えて粘度や比重を調整してからメタン発酵槽に投入することもできる。 One embodiment of the present invention is shown in FIG. In this apparatus, a device for removing inappropriate methane fermentation is provided in the previous stage of the methane fermentation tank. Organic waste such as kitchen waste is put into a stirring and separation tank. In the agitation / separation tank, inadequate methane fermentation materials such as eggshell in the garbage are settled and discharged continuously or intermittently from the lower outlet. Organic waste from which methane fermentation unsuitables have been removed is supplied to the methane fermenter and subjected to methane fermentation, and the fermentation liquor is continuously or intermittently extracted from the methane fermenter and sent to the membrane separation tank. . Since the concentration of organic substances such as SS and COD Mn is low in the treated water in which the fermentation liquid is separated into the treated water and the fermented sludge in the membrane separation tank, post-treatment such as sewage discharge is simplified. The biogas consisting mainly of methane and carbon dioxide generated in the methane fermentation tank can be used as power generation fuel. Part of the biogas is sent to the membrane separation tank via a blower or the like and used for aeration. Garbage etc. can be directly put into the methane fermentation tank together with water if necessary, or can be put into the methane fermentation tank after adjusting the viscosity and specific gravity by adding water in the adjustment tank.
本発明の別の実施態様を図2に示す。この装置は、メタン発酵槽と膜分離槽との間にメタン発酵不適物の除去装置が設けられている。生ごみ等の有機性廃棄物がメタン発酵槽に投入されてメタン発酵が行われ、メタン発酵槽からは発酵液が連続的あるいは間欠的に抜き出されて攪拌分離槽に供給される。攪拌分離槽内では生ごみ中の卵殻等のメタン発酵不適物が沈降して下端の排出口から連続的あるいは間欠的に排出される。メタン発酵不適物が除去された発酵液は膜分離槽に送られて処理水と発酵汚泥に分離される。なお、メタン発酵不適物の除去装置は、図1と図2に示す位置の両方に設けることもできる。 Another embodiment of the present invention is shown in FIG. In this apparatus, a device for removing inappropriate methane fermentation is provided between the methane fermentation tank and the membrane separation tank. Organic waste such as garbage is put into the methane fermentation tank to perform methane fermentation, and the fermentation liquor is continuously or intermittently extracted from the methane fermentation tank and supplied to the stirring and separation tank. In the agitation / separation tank, inadequate methane fermentation materials such as eggshell in the garbage are settled and discharged continuously or intermittently from the lower outlet. The fermentation liquor from which methane fermentation inappropriate substances have been removed is sent to a membrane separation tank and separated into treated water and fermentation sludge. In addition, the removal apparatus of a methane fermentation unsuitable thing can also be provided in both the positions shown in FIG. 1 and FIG.
系から取り出される発酵汚泥は、メタン発酵槽に返送されるが、焼却処理してもよく、あるいは、乾燥して肥料や燃料に用いてもよい。卵殻、貝殻等は洗浄してチョーク原料とかセメント原料などに利用できる。 Fermented sludge taken out from the system is returned to the methane fermentation tank, but may be incinerated, or dried and used as fertilizer or fuel. Egg shells, shells, etc. can be washed and used as chalk raw materials or cement raw materials.
実施例1
図1に示す装置を用いた。
Example 1
The apparatus shown in FIG. 1 was used.
メタン発酵槽は容積1,500Lの箱型の密閉槽を、そして、膜分離槽には濾過面積0.1m2×5個の精密濾過膜を装着したものを用いた。メタン発酵不適物の除去装置には図3に示すものを用いた。この装置は、攪拌分離槽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のところにスラリーの原料投入口4が、底部2のやや上には卵殻(メタン発酵不適物)を除去した分離液排出口5が、そして底部2の中心には卵殻を含む濃縮液排出口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。攪拌分離槽の容積は約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。攪拌分離槽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 methane fermentation tank used was a box-shaped sealed tank with a capacity of 1,500 L, and the membrane separation tank was equipped with a microfiltration membrane having a filtration area of 0.1 m 2 × 5. The apparatus shown in FIG. 3 was used as an apparatus for removing inappropriate methane fermentation. In this apparatus, the stirring /
この装置を用い、家庭系生ごみに水を加えて、粘度0.85〜1.35Pa・s、比重約1.0g/mL、TS(蒸発残留物)3.6〜5.1質量%、卵殻濃度0.7〜3.6g・dry卵殻/kg・wet原料としたスラリーを、攪拌分離槽に投入した。卵殻を沈降分離して、卵殻が除去された分離液をメタン発酵槽に供給してメタン発酵を行った。得られた発酵液を膜分離槽に供給して処理水と発酵汚泥とに分離した。ここで、メタン発酵不適物の除去装置において、攪拌分離槽内の攪拌羽根の段数、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, water is added to household waste, viscosity is 0.85 to 1.35 Pa · s, specific gravity is about 1.0 g / mL, TS (evaporation residue) 3.6 to 5.1% by mass, An slurry having an eggshell concentration of 0.7 to 3.6 g · dry eggshell / kg · wet raw material was put into a stirring separation tank. The eggshell was settled and separated, and the separation liquid from which the eggshell had been removed was supplied to a methane fermentation tank to perform methane fermentation. The obtained fermentation broth was supplied to a membrane separation tank and separated into treated water and fermentation sludge. Here, in the apparatus for removing unsuitable materials for methane fermentation, the eggshell separation test was performed by changing the number of stirrer blades in the stirrer / separation tank, the blade diameter, the height from the bottom of the lower blade, and the blade interval. .
結果を表1に示した。ここで、評価として、次式で表される卵殻除去率を算出し、除去率が80%以上を◎、70〜80%を○、50〜70%を△、50%以下を×とした。
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)が卵殻とともに堆積し、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。
The results are shown in Table 1. Here, as an evaluation, the eggshell removal rate represented by the following formula was calculated, and the removal rate was 80% or more: ◎, 70-80%: ○, 50-70%: Δ, 50% or less: x.
Under
実施例2
図2に示す装置を用いた。メタン発酵槽は容積1,500Lの箱型の密閉槽を、そして、膜分離槽には濾過面積0.1m2×5個の精密濾過膜を装着したものを用いた。メタン発酵不適物の除去装置には実施例1と同様に図3に示すものを用いた。攪拌分離槽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のところにメタン発酵槽からの発酵液の原料投入口4が、底部2のやや上には卵殻(メタン発酵不適物)を除去した分離液排出口5が、そして底部2の中心には卵殻を含む濃縮液排出口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。攪拌分離槽の容積は約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。攪拌分離槽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。
Example 2
The apparatus shown in FIG. 2 was used. The methane fermentation tank used was a box-shaped sealed tank having a capacity of 1,500 L, and the membrane separation tank was equipped with a microfiltration membrane having a filtration area of 0.1 m 2 × 5. As in Example 1, the apparatus shown in FIG. The stirring /
メタン発酵させる有機性廃棄物として、家庭系生ごみに水を加えて、粘度1.2〜1.5Pa・s、比重約1.0g/mL、TS約6質量%、卵殻濃度2.7〜3.3g・dry卵殻/kg・wet原料としたスラリーをメタン発酵槽に100kg/日の速度で投入して38℃でメタン発酵を行った。メタン発酵槽からはTS2.0〜2.5質量%の発酵液を300kg/日の速度で抜き出して攪拌分離槽に入れ、卵殻を沈降分離し、卵殻が除去された発酵液を膜分離槽に送り、分離された発酵汚泥をメタン発酵槽に循環した。攪拌分離槽の攪拌羽根の段数、羽根の径、下段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。
結果を表2に示す。ここで、評価は、実施例1と同様である。
As organic waste to be fermented with methane, water is added to household garbage, viscosity 1.2-1.5 Pa · s, specific gravity about 1.0 g / mL, TS about 6% by mass, eggshell concentration 2.7 ~ The slurry made into 3.3g * dry eggshell / kg * wet raw material was thrown into the methane fermentation tank at the rate of 100 kg / day, and methane fermentation was performed at 38 degreeC. From the methane fermenter, TS 2.0-2.5 mass% of the fermented liquid is extracted at a rate of 300 kg / day, put into a stirring separation tank, the eggshell is settled and separated, and the fermented liquid from which the eggshell has been removed is put into a membrane separation tank. The fermented sludge sent and separated was circulated to the methane fermentation tank. The eggshell separation test was performed by changing the number of stirring blades in the stirring / separation tank, the diameter of the blades, the height from the bottom of the lower blades, and the distance between the blades.
The results are shown in Table 2. Here, the evaluation is the same as in Example 1.
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 methane fermentation inadequate containing calcium from organic waste such as garbage discharged from households and restaurants, etc., a method for methane fermentation of these organic waste Can be used widely.
1 攪拌分離槽
2 底部
3 脚部
4 原料投入口
5 分離液排出口
6 濃縮液排出口
7 攪拌機
8 攪拌羽根
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