JP2952738B2 - High-concentration organic matter treatment method - Google Patents
High-concentration organic matter treatment methodInfo
- Publication number
- JP2952738B2 JP2952738B2 JP12805793A JP12805793A JP2952738B2 JP 2952738 B2 JP2952738 B2 JP 2952738B2 JP 12805793 A JP12805793 A JP 12805793A JP 12805793 A JP12805793 A JP 12805793A JP 2952738 B2 JP2952738 B2 JP 2952738B2
- Authority
- JP
- Japan
- Prior art keywords
- organic matter
- fermenter
- fermentation
- carrier
- extraction residue
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
- 239000005416 organic matter Substances 0.000 title claims description 18
- 238000000034 method Methods 0.000 title claims description 11
- 239000007788 liquid Substances 0.000 claims description 15
- 239000000126 substance Substances 0.000 claims description 14
- 241000533293 Sesbania emerus Species 0.000 claims description 9
- 244000005700 microbiome Species 0.000 claims description 7
- 238000010564 aerobic fermentation Methods 0.000 claims description 4
- 238000009423 ventilation Methods 0.000 claims 1
- 238000000605 extraction Methods 0.000 description 20
- 238000000855 fermentation Methods 0.000 description 18
- 230000004151 fermentation Effects 0.000 description 18
- 230000029087 digestion Effects 0.000 description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 10
- 239000002351 wastewater Substances 0.000 description 8
- 230000000694 effects Effects 0.000 description 5
- 239000002023 wood Substances 0.000 description 5
- 241001148470 aerobic bacillus Species 0.000 description 4
- 229920005610 lignin Polymers 0.000 description 4
- 230000035699 permeability Effects 0.000 description 4
- 238000001914 filtration Methods 0.000 description 3
- 239000011810 insulating material Substances 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N phenol group Chemical group C1(=CC=CC=C1)O ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 3
- 229920000642 polymer Polymers 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 238000011049 filling Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 235000019645 odor Nutrition 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 241000196324 Embryophyta Species 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 238000004332 deodorization Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- 230000001771 impaired effect Effects 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 239000012774 insulation material Substances 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 150000002989 phenols Chemical class 0.000 description 1
- 230000000644 propagated effect Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000003516 soil conditioner Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
Classifications
-
- 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
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は高濃度有機排水中の有機
物を、担体に付着する微生物との発酵消化作用により処
理する方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating organic matter in high-concentration organic wastewater by fermentation and digestion with microorganisms adhering to a carrier.
【0002】[0002]
【従来の技術】現在、高濃度有機排水及び有機固形物を
処理する方法としては、これら有機物を木質細片(おが
屑)や活性炭よりなる微生物担体と混合して発酵消化さ
せることが行われている。2. Description of the Related Art At present, as a method for treating high-concentration organic wastewater and organic solids, these organic substances are mixed with a microbial carrier made of wood chips (sawdust) or activated carbon and fermented and digested. .
【0003】この方法によれば、担体と混合した有機物
は、担体に担持されている微生物によって発酵消化さ
れ、炭酸ガス、水、無機塩、アンモニアなどに分解され
てドレンとして排出される。According to this method, an organic substance mixed with a carrier is fermented and digested by microorganisms carried on the carrier, decomposed into carbon dioxide, water, inorganic salts, ammonia, etc., and discharged as drain.
【0004】この際、木質細片も有機物であることから
その一部が発酵消化作用によって分解され、木質中のフ
ェノール性高分子であるリグニンがドレン中に排出され
る。フェノール類は排出規制物質であるとともに、リグ
ニンは植物の根腐れを引き起こす原因となるので、ドレ
ンを2次処理しなければ放流することはできない。At this time, since the wood fragments are also organic substances, a part thereof is decomposed by fermentation and digestion, and lignin, which is a phenolic polymer in the wood, is discharged into the drain. Phenols are emission control substances, and lignin causes root rot of plants. Therefore, drainage cannot be released without secondary treatment of drainage.
【0005】また、発酵処理中に発酵臭が発生するの
で、処理装置を設置する場所によっては大型の脱臭槽が
必要となる。[0005] Further, since fermentation odor is generated during the fermentation treatment, a large deodorization tank is required depending on the place where the treatment apparatus is installed.
【0006】活性炭はその吸着作用から担体として使用
できるが、吸着した有機物を除去して吸着能力を再生し
なければならず、その再生には高温下で吸着成分を焼却
するなどの高価な装置が必要とされる。さらに、活性炭
は有機物と混合するとかたまり易く、塊状となって通気
性が損なわれ、好気性菌の活動が阻害され、また、攪拌
機には動力の大なるモータが必要とされる。[0006] Activated carbon can be used as a carrier because of its adsorption function. However, it is necessary to remove adsorbed organic substances to regenerate the adsorbing ability. Needed. Further, activated carbon is liable to clump when mixed with an organic substance, and becomes clumpy, impairs air permeability, inhibits the activity of aerobic bacteria, and requires a high-power motor for the stirrer.
【0007】[0007]
【発明が解決しようとする課題】高濃度の有機物の発酵
消化処理に関し、 a.フェノール性高分子であるリグニンの排出を防止す
る b.通気性を確保することにより好気性菌の活動を促進
し、処理能力の向上を図る C.攪拌動力の低減を図る d.コーヒー豆のコーヒー液抽出残滓の消化処理を図る ことを目的とする。SUMMARY OF THE INVENTION The present invention relates to a fermentation digestion treatment of high-concentration organic matter, comprising: a. Prevent the emission of lignin, a phenolic polymer b. B. Promote the activity of aerobic bacteria by ensuring air permeability, and improve treatment capacity. Reduce stirring power d. The purpose is to digest coffee liquid extraction residue from coffee beans.
【0008】[0008]
【課題を解決するための手段】上記目的を達成するため
に、本発明の高濃度有機物処理方法は、通気口、攪拌装
置を備える発酵槽内にコーヒー豆のコーヒー液抽出残滓
を微生物の担体として充填し、この中に有機物を供給し
て有機物と担体とを前記攪拌装置によって混合しながら
前記通気口から空気を連続供給し、高温、好気性発酵さ
せることにより有機物を分解させることを特徴としてい
る。In order to achieve the above object, the present invention provides a method for treating a high-concentration organic substance, comprising the steps of: extracting coffee liquid residue of coffee beans into a fermenter having a vent and a stirrer; Filling, supplying organic matter therein, continuously supplying air from the vent while mixing the organic matter and the carrier with the stirring device, and decomposing the organic matter by high-temperature, aerobic fermentation. .
【0009】[0009]
【作用】コーヒー液の抽出残滓と攪拌、混合された有機
物は発酵に必要な空気を通気口から与えられ、高温・好
気の条件下で発酵消化される。担体たるコーヒー豆のコ
ーヒー液抽出残滓も発酵消化によって一部消化され、消
化処理後の抽出残滓は殆ど無機物となる。The organic matter mixed with the extraction residue of the coffee liquor and agitated and mixed is provided with air required for fermentation through a vent, and is fermented and digested under high temperature and aerobic conditions. The extraction residue of coffee liquid of coffee beans as a carrier is also partially digested by fermentation digestion, and the extraction residue after the digestion treatment is almost inorganic.
【0010】また、コーヒー液の抽出残滓は有機物と混
合されてもかたまり難く、通気性が損なわれない。その
結果、好気性菌の活動が活発になり、有機物処理能力が
向上する。[0010] Further, even if the extraction residue of the coffee liquor is mixed with an organic substance, it is hard to clump and the air permeability is not impaired. As a result, the activity of the aerobic bacteria becomes active, and the organic matter treatment capacity is improved.
【0011】[0011]
【実施例】以下本発明による高濃度有機物処理方法の具
体例を図1に基づいて詳細に説明する。図1は本発明方
法に使用する装置の一具体例を示すもので、図中の符号
1は発酵槽、3は微生物を担持するための担体たるコー
ヒー豆のコーヒー液抽出残滓、4は有機排水とコーヒー
液抽出残滓3とを混合するための攪拌装置、5は発酵槽
1内に空気を連続供給するブロア、9は発酵槽内に有機
排水を供給するための流入管である。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A specific example of the method for treating a high-concentration organic substance according to the present invention will be described below in detail with reference to FIG. FIG. 1 shows a specific example of an apparatus used in the method of the present invention. In the figure, reference numeral 1 denotes a fermentation tank, 3 denotes a coffee liquid extraction residue of coffee beans which is a carrier for supporting microorganisms, and 4 denotes an organic wastewater. Is a stirrer for mixing the liquid and the coffee liquid extraction residue 3, a blower 5 for continuously supplying air into the fermenter 1, and an inflow pipe 9 for supplying organic wastewater into the fermenter.
【0012】発酵槽1は断熱材2で囲まれており、槽内
の下部には処理中に発生した水分を分離するために割栗
石6a、砂礫6b等からなる濾過層6を設け、発酵槽1
の底には濾過水を排出するためのドレン口7を設けてあ
る。The fermenter 1 is surrounded by a heat insulating material 2, and a filter layer 6 made of cracked stone 6a, gravel 6b or the like is provided at a lower portion of the tank to separate water generated during the treatment. 1
Is provided with a drain port 7 for discharging filtered water.
【0013】流入管9から供給された有機排水と、発酵
槽1内に充填されたコーヒー液抽出残滓3とを混合する
ための攪拌装置4は、発酵槽1上部に設けられたモータ
Mによって回転させられるようになっている。A stirrer 4 for mixing the organic wastewater supplied from the inflow pipe 9 and the coffee liquid extraction residue 3 filled in the fermenter 1 is rotated by a motor M provided on the upper part of the fermenter 1. It is made to be made.
【0014】発酵槽1下部の濾過層6側部にあけた通気
口5aには外部からの空気を連続供給するためのブロア
5を接続してあり、また発酵槽1の上部には発酵によっ
て発生する臭気を処理するための脱臭器8を設けてあ
る。A blower 5 for continuously supplying air from the outside is connected to a vent 5a opened in the lower part of the fermenter 1 on the side of the filtration layer 6, and the upper part of the fermenter 1 is formed by fermentation. A deodorizer 8 is provided for treating odors.
【0015】次にこのように構成される発酵消化槽によ
って高濃度有機物を高温好気性処理する手順を説明す
る。発酵槽1内にコーヒー液抽出残滓3を充填した後、
この抽出残滓3に流入管9を通して外部から高濃度有機
排水を供給する(有機物が固形のばあいにはコンベア等
によって発酵槽1内に供給する)。この有機排水の供給
は微生物との接触により発酵消化に必要とされる処理時
間を基に計算した間隔をおいて間欠的に行う。Next, a procedure for subjecting high-concentration organic matter to high-temperature aerobic treatment by the fermentation digester constructed as described above will be described. After filling the fermenter 1 with the coffee liquid extraction residue 3,
High-concentration organic wastewater is supplied to the extraction residue 3 from the outside through an inflow pipe 9 (if the organic matter is solid, it is supplied into the fermenter 1 by a conveyor or the like). The supply of the organic wastewater is performed intermittently at intervals calculated based on the treatment time required for fermentation and digestion by contact with microorganisms.
【0016】続いて、攪拌装置4によってコーヒー液抽
出残滓3と有機排水の混合物を撹拌し、好気性微生物が
均一に繁殖するようにするとともに、ブロア5により通
気口5aを通して50〜400リットル/分・m3 の空
気を発酵槽1内に連続供給し、好気性発酵を促進させ
る。Subsequently, the mixture of the coffee liquor extraction residue 3 and the organic wastewater is stirred by the stirrer 4 so that the aerobic microorganisms can be propagated uniformly, and the blower 5 allows the mixture to flow through the vent 5a at 50 to 400 l / min. -Continuous supply of m 3 air into the fermenter 1 to promote aerobic fermentation.
【0017】ブロア5からの充分な空気の供給と断熱材
2での保温により、発酵槽1内は適度な酸素・温度条件
が保たれて高温、好気性発酵が起こり、この発酵が促進
されて有機物を消化、分解する。この際、担体の含水率
を80%未満となるように有機物に含まれる水分を調節
する。含水率がこれ以上になると発酵条件がくずれ、発
酵が停止する。By supplying sufficient air from the blower 5 and keeping the heat in the heat insulating material 2, moderate oxygen and temperature conditions are maintained in the fermenter 1 and high-temperature, aerobic fermentation occurs, and this fermentation is promoted. Digest and decompose organic matter. At this time, the water content of the organic matter is adjusted so that the water content of the carrier is less than 80%. If the water content exceeds this, the fermentation conditions are disrupted and the fermentation stops.
【0018】有機物中の余分な水分はコーヒー液抽出残
滓3に吸収、保水され、好気性微生物が活発に活動し、
槽内は50〜70℃の高温を発生する。有機物が分解さ
れると水分が発生するが、発酵によって発酵槽内が高温
となるためにこの水分は水蒸気となって蒸発し、若干の
水分は濾過層6を経てドレン口7から槽外部へ排出され
る。The excess water in the organic matter is absorbed and retained in the coffee liquor extraction residue 3, and the aerobic microorganisms are actively activated.
A high temperature of 50 to 70 ° C. is generated in the tank. When the organic matter is decomposed, water is generated. However, since the temperature in the fermenter becomes high due to the fermentation, this water becomes vapor and evaporates, and a small amount of water is discharged from the drain port 7 through the filtration layer 6 to the outside of the tank. Is done.
【0019】発酵消化処理の際、担体たるコーヒー豆の
コーヒー液抽出残滓もその一部が消化されるので、消化
処理にともなって抽出残滓を補充する必要がある。コー
ヒー液抽出残滓の消化速度は被処理物たる有機物に比較
して遅いので、被処理有機物250kgに対し、抽出残
滓150kg程度を補充する。In the fermentation digestion treatment, a part of the coffee liquid extraction residue of the coffee beans as a carrier is also digested, so it is necessary to supplement the extraction residue with the digestion treatment. Since the digestion rate of the coffee liquid extraction residue is slower than that of the organic substance as the substance to be treated, about 150 kg of the extraction residue is supplemented to 250 kg of the organic substance to be treated.
【0020】なお、発酵槽の直径が5〜6mを超えるば
あいには処理容量あたりの表面積が小さくなるので、断
熱材2を設ける必要はない。When the diameter of the fermenter exceeds 5 to 6 m, the heat insulating material 2 does not need to be provided because the surface area per processing capacity becomes small.
【0021】表1は担体として木質細片、活性炭、コー
ヒー豆のコーヒー液抽出残滓を使用したばあいにおける
有機物たる残飯の発酵消化処理を行った結果を示す実験
データである。Table 1 shows experimental data showing the results of fermentation and digestion of organic residue as a carrier when wood chips, activated carbon, and coffee liquid extraction residue of coffee beans are used as a carrier.
【0022】[0022]
【表1】 このデータより、担体としてコーヒー豆のコーヒー液抽
出残滓を使用したばあいには、木質細片のばあいの約
3.9倍、活性炭のばあいの約4.2倍の処理能力があ
ることが判明した。[Table 1] From this data, it was found that when the coffee liquid extraction residue of coffee beans was used as the carrier, the processing capacity was about 3.9 times that of wood chips and about 4.2 times that of activated carbon. did.
【0023】[0023]
【発明の効果】本発明方法によれば次のような効果を奏
し得る。高濃度の有機物の発酵消化処理に関し、 a.ドレン中に、フェノール性高分子であるリグニンが
排出するのが防止されるので、ドレンを2次処理する必
要がなく、その装置が不要である b.有機物と混合してもかたまりにくいので通気性が確
保され、好気性菌の活動が促進されて、その結果処理能
力が向上させられる C.前述のようにかたまりにくいので、攪拌動力が低減
させられ、低コストに処理できる また現在、コーヒー豆のコーヒー液抽出残滓は産業廃棄
物として処理しているが、本発明方法によればコーヒー
豆のコーヒー抽出残滓も一部消化され、さらに処理後の
担体は殆どが無機物となるので、土壌改良剤として転用
できる。According to the method of the present invention, the following effects can be obtained. Regarding fermentation digestion treatment of high-concentration organic matter, a. Since lignin, which is a phenolic polymer, is prevented from being discharged into the drain, there is no need for secondary treatment of the drain, and no equipment is required. B. B. Since it is hard to clump even when mixed with organic matter, air permeability is ensured, the activity of aerobic bacteria is promoted, and as a result, the processing capacity is improved. As described above, since it is difficult to agglomerate, the stirring power is reduced and it can be processed at low cost.Also, at present, the coffee liquid extraction residue of coffee beans is treated as industrial waste. The coffee extract residue is also partially digested, and most of the carrier after the treatment becomes inorganic, so that it can be diverted as a soil conditioner.
【図1】本発明方法に使用する発酵槽の実施例を示す断
面図。FIG. 1 is a sectional view showing an embodiment of a fermenter used in the method of the present invention.
1 発酵槽 2 断熱材 3 コーヒー液抽出残滓 4 攪拌装置 5 ブロア 6 濾過層 7 ドレン口 8 脱臭器 9 流入管 DESCRIPTION OF SYMBOLS 1 Fermenter 2 Insulation material 3 Coffee liquid extraction residue 4 Stirrer 5 Blower 6 Filtration layer 7 Drain port 8 Deodorizer 9 Inflow pipe
───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.6,DB名) C02F 3/08 C02F 3/10 ──────────────────────────────────────────────────続 き Continued on the front page (58) Field surveyed (Int.Cl. 6 , DB name) C02F 3/08 C02F 3/10
Claims (1)
ヒー豆のコーヒー液抽出残滓を微生物の担体として充填
し、この中に有機物を供給して有機物と担体とを前記攪
拌装置によって混合しながら前記通気口から空気を連続
供給し、高温、好気性発酵させることにより有機物を分
解させることを特徴とする高濃度有機物処理方法。1. A fermenter having a vent and a stirrer is filled with a coffee liquid extract residue of coffee beans as a carrier for microorganisms, and an organic substance is supplied into the fermenter, and the organic substance and the carrier are mixed by the stirrer. A high-concentration organic matter treatment method, characterized in that air is continuously supplied from the ventilation port and organic matter is decomposed by high-temperature, aerobic fermentation.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12805793A JP2952738B2 (en) | 1993-04-30 | 1993-04-30 | High-concentration organic matter treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12805793A JP2952738B2 (en) | 1993-04-30 | 1993-04-30 | High-concentration organic matter treatment method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH06315694A JPH06315694A (en) | 1994-11-15 |
| JP2952738B2 true JP2952738B2 (en) | 1999-09-27 |
Family
ID=14975419
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP12805793A Expired - Lifetime JP2952738B2 (en) | 1993-04-30 | 1993-04-30 | High-concentration organic matter treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2952738B2 (en) |
-
1993
- 1993-04-30 JP JP12805793A patent/JP2952738B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH06315694A (en) | 1994-11-15 |
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