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JP2015058401A - Wastewater treatment apparatus - Google Patents

Wastewater treatment apparatus Download PDF

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JP2015058401A
JP2015058401A JP2013193839A JP2013193839A JP2015058401A JP 2015058401 A JP2015058401 A JP 2015058401A JP 2013193839 A JP2013193839 A JP 2013193839A JP 2013193839 A JP2013193839 A JP 2013193839A JP 2015058401 A JP2015058401 A JP 2015058401A
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tank
treatment apparatus
sludge
water
separation
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JP2015058401A5 (en
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梅沢 浩之
Hiroyuki Umezawa
浩之 梅沢
立木 悦二
Etsuji Tachiki
悦二 立木
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Panasonic Corp
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Activated Sludge Processes (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a wastewater treatment apparatus which recovers metals in wastewater by a simple treatment process.SOLUTION: In a wastewater treatment apparatus which recovers metals by a simple treatment process, hardly biodegradable substances contained in wastewater are degraded to easily degradable substances by air added with low-concentration ozone, the easily degradable substances are treated and metals contained in the wastewater are adsorbed and precipitated by biological treatment in a membrane separation activated sludge tank 7, and only the precipitated metal fine particles are recovered.

Description

本発明は、金属を含有した生物難分解性有機排水の処理と金属の回収に関するものである。   The present invention relates to treatment of biologically incurable organic wastewater containing metal and metal recovery.

現在、産業廃棄物を減らすこと、また産業廃棄物を分別し再利用することまたは産業廃棄物を自然界に放出させないことは、エコロジーの観点から重要なテーマであり、21世紀の企業課題である。特にレアメタル類や貴金属類は枯渇の問題あり、廃棄物からの回収は重要である。   At present, reducing industrial waste, separating and reusing industrial waste, or not releasing industrial waste to the natural world is an important theme from the viewpoint of ecology and is a corporate issue in the 21st century. In particular, rare metals and precious metals have a depletion problem, and recovery from waste is important.

この産業廃棄物の中には、被除去物が含まれた色々な流体がある。これらは、汚水、排水、廃液等の色々な言葉で表現されているが、以下、水や薬品等の流体中に被除去物である物質が含まれているものを排水と呼び説明する。   Among these industrial wastes, there are various fluids containing the objects to be removed. These are expressed in various words such as sewage, drainage, and waste liquid. Hereinafter, a substance that is a substance to be removed in a fluid such as water or chemicals will be referred to as drainage.

これらの排水は、高価な濾過処理装置等で前記被除去物が取り除かれ、排水がきれいな流体となり再利用される。また、分別された被除去物または濾過できず残ったものは産業廃棄物として処理されている。廃棄物の中には金属が含まれる場合があり、有用な金属は更に回収処理が実施さている。これらの有用な金属を含む排水には生物難分解性物質を含む排水もあり、この場合は更に分解処理が追加され実施される。   These waste water is reused by removing the object to be removed by an expensive filtration device or the like, and the waste water becomes a clean fluid. Further, the separated objects to be removed or those that cannot be filtered are treated as industrial waste. Waste may contain metals, and useful metals are further recovered. The waste water containing these useful metals includes waste water containing biodegradable substances. In this case, further decomposition treatment is performed.

従来の生物難分解性有機排水の処理方法としては、オゾンや過酸化水素などの薬剤を添加した促進酸化処理が行われている。促進酸化処理では、過剰な薬剤を添加し生物難分解性物質を分解した後、残留した薬剤を無害化して後段で生物処理をしている(たとえば特許文献1、2参照)。その後、排水に含まれる白金などの金属類は、晶析反応を利用して塩化物としたり(たとえば特許文献3参照)、金属イオンを還元する微生物により金属微粒子として回収している(たとえば特許文献4参照)。   As a conventional method for treating biologically difficult-to-decompose organic wastewater, accelerated oxidation treatment with addition of chemicals such as ozone and hydrogen peroxide is performed. In the accelerated oxidation treatment, an excessive drug is added to decompose the biodegradable substance, the remaining drug is rendered harmless, and the biological treatment is performed later (for example, refer to Patent Documents 1 and 2). Thereafter, metals such as platinum contained in the waste water are converted into chlorides using a crystallization reaction (see, for example, Patent Document 3) or recovered as metal fine particles by a microorganism that reduces metal ions (for example, Patent Document). 4).

特許第372512号公報Japanese Patent No. 372512 特開2002−166275号公報JP 2002-166275 A 特許第3479483号公報Japanese Patent No. 3479483 特開2013−13403号公報JP 2013-13403 A

このような従来技術では、生物難分解性排水に金属イオンや金属錯体が含有される場合、難分解性物質をオゾンなどの薬剤で酸化分解した後、金属イオンや金属錯体を回収する晶析などの処理プロセスを実施する必要があり、排水処理工程が複雑になり金属や金属イオン、金属錯体を回収するには効率が低かった。また、金属類は汚泥に含まれ含有率が低い状態で回収される場合が多く、汚泥から高濃度で回収するため焼却処理なども必要であった。   In such a conventional technique, when metal ions or metal complexes are contained in the biologically degradable wastewater, crystallization of recovering metal ions or metal complexes after oxidative decomposition of the hardly decomposable substance with a chemical such as ozone, etc. Therefore, the wastewater treatment process becomes complicated, and the efficiency of recovering metals, metal ions, and metal complexes is low. In addition, metals are often contained in sludge and recovered in a low content, and incineration is necessary to recover from sludge at a high concentration.

そこで、本発明は上記の課題を解決するものであり、排水中の金属類を簡単な処理プロセスにより回収する排水処理装置を提供することを目的にしている。   Then, this invention solves said subject and it aims at providing the waste_water | drain processing apparatus which collect | recovers the metals in waste_water | drain by a simple processing process.

そしてこの目的を達成するため本発明では、オゾン添加空気により金属を含有する生物難分解性排水を分解して分解水を得る分解槽と、微生物により前記分解水から金属を微粒子として還元して金属含有汚泥を含む濃縮水を得る膜分離活性汚泥槽と、前記濃縮水中の汚泥を沈降させて上澄み液を得る沈降分離槽と、分離部により前記上澄み液から金属を回収する分離部を備えることを特徴とする排水処理装置としたものであり。これにより所期の目的を達成するものである。   And in order to achieve this object, in the present invention, a decomposition tank for decomposing a biologically difficult-to-decompose wastewater containing metal with ozone-added air to obtain decomposition water; A membrane separation activated sludge tank for obtaining concentrated water containing sludge, a sedimentation separation tank for obtaining a supernatant liquid by settling sludge in the concentrated water, and a separation part for recovering metal from the supernatant liquid by a separation part. This is a featured wastewater treatment device. This achieves the intended purpose.

本発明によれば、金属類を回収するための複雑な処理と制御を実施することなく、金属を回収することでき、回収工程を容易にするという効果をえることができる。   ADVANTAGE OF THE INVENTION According to this invention, without performing the complicated process and control for collect | recovering metals, a metal can be collect | recovered and the effect of making a collection | recovery process easy can be acquired.

本発明の実施形態1の白金含有生物難分解性排水処理装置の構成図Configuration diagram of platinum-containing biodegradable wastewater treatment apparatus of Embodiment 1 of the present invention

本発明の請求項1記載の排水処理装置は、オゾン添加空気により金属を含有する生物難分解性排水を分解して分解水を得る分解槽と、微生物により前記分解水から金属を微粒子として還元して金属含有汚泥を含む濃縮水を得る膜分離活性汚泥槽と、前記濃縮水中の汚泥を沈降させて上澄み液を得る沈降分離槽と、分離部により前記上澄み液から金属を回収する分離部を備えるものである。   The waste water treatment apparatus according to claim 1 of the present invention is a decomposition tank for decomposing biodegradable waste water containing metal by ozone-added air to obtain decomposition water, and reducing metal from the decomposition water as fine particles by microorganisms. A membrane separation activated sludge tank for obtaining concentrated water containing metal-containing sludge, a sedimentation separation tank for obtaining a supernatant liquid by settling sludge in the concentrated water, and a separation part for recovering metal from the supernatant liquid by a separation part. Is.

これにより、簡単な処理装置と回収工程で排水処理と排水中の金属の回収を効率よく行えるという効果を奏する。   Thereby, there exists an effect that waste water treatment and the collection | recovery of the metal in waste water can be performed efficiently with a simple processing apparatus and a collection process.

また、請求項2記載の排水処理装置は、沈降分離槽で沈降した汚泥を膜分離活性汚泥槽へ戻すことにより、金属類を吸着する微生物の量を減少することなく、金属類の回収を継続することができるという効果を奏する。   Further, the wastewater treatment apparatus according to claim 2 continues the recovery of the metals without reducing the amount of microorganisms adsorbing the metals by returning the sludge settled in the sedimentation separation tank to the membrane separation activated sludge tank. There is an effect that can be done.

また、請求項3記載の排水処理装置は、金属が回収された残処理水を膜分離活性汚泥槽へ戻すことにより、生物処理に必要な有機物を供給するという効果を奏する。   Moreover, the waste water treatment apparatus according to claim 3 has an effect of supplying the organic matter necessary for biological treatment by returning the residual treated water from which the metal has been recovered to the membrane separation activated sludge tank.

また、請求項4記載の排水処理装置は、分離部に遠心分離装置を用いることにより、比重の重い金属を効率良く分離することができるという効果を奏する。   Moreover, the waste water treatment apparatus according to claim 4 has an effect that metal having a high specific gravity can be efficiently separated by using a centrifugal separator in the separation section.

また、請求項5記載の排水処理装置は、分離部に精密ろ過膜を用いることにより、微細な粒子となる金属でも効率よく分離することができるという効果を奏する。   Moreover, the waste water treatment apparatus of Claim 5 has the effect that it can isolate | separate efficiently even the metal used as a fine particle by using a microfiltration membrane for a separation part.

また、請求項6記載の排水処理装置は、分離部に用いる精密ろ過膜の孔径が0.4μm以下であることにより、生物汚泥を分離できるという効果を奏する。   Moreover, the waste water treatment apparatus of Claim 6 has an effect that biological sludge can be separated when the pore diameter of the microfiltration membrane used in the separation section is 0.4 μm or less.

以下、本発明の実施の形態について図面を参照しながら説明する。   Hereinafter, embodiments of the present invention will be described with reference to the drawings.

(実施の形態1)
図1に示すように、排水処理装置は、オゾン添加空気4により金属を含有する生物難分解性の排水1を分解して分解水6を得る分解槽2と、微生物により分解水6から金属を微粒子として還元して金属含有汚泥を含む濃縮水14を得る膜分離活性汚泥槽7と、濃縮水14中の汚泥を沈降させて上澄み液17と濃縮水14を得る沈降分離槽15と、分離部18により上澄み液17から金属を回収する分離部18を備え構成している。
(Embodiment 1)
As shown in FIG. 1, the wastewater treatment apparatus includes a decomposition tank 2 for decomposing biologically degradable wastewater 1 containing metal by ozone-added air 4 to obtain decomposition water 6, and metal from decomposition water 6 by microorganisms. Membrane separation activated sludge tank 7 that obtains concentrated water 14 containing metal-containing sludge by reducing as fine particles, sedimentation separation tank 15 that sediments sludge in concentrated water 14 to obtain supernatant liquid 17 and concentrated water 14, and separation unit A separation unit 18 for recovering metal from the supernatant liquid 17 is provided.

分解槽2はオゾン添加空気4が散気される分解槽散気管3を備え構成される。分解槽2により得られた分解水6が導入される膜分離活性汚泥槽7は、浮遊汚泥8が貯留され、空気10を散気する活性汚泥槽散気管9が底部に設置される。更に、濃縮水14からろ過水13を吸引するための浸漬膜ユニット12を備え構成される。   The decomposition tank 2 includes a decomposition tank diffusion tube 3 through which ozone-added air 4 is diffused. In the membrane separation activated sludge tank 7 into which the cracked water 6 obtained from the decomposition tank 2 is introduced, the floating sludge 8 is stored, and the activated sludge tank aeration pipe 9 that diffuses air 10 is installed at the bottom. Furthermore, it comprises an immersion membrane unit 12 for sucking filtered water 13 from the concentrated water 14.

上記構成において、排水処理装置が生物難分解性の排水1から金属を回収する動作を説明する。   The operation | movement which collect | recovers metals from the waste_water | drain 1 of a biodegradable waste water treatment apparatus in the said structure is demonstrated.

排水1が分解槽2に供給されると、分解槽2は、分解槽散気管3より、オゾン添加空気4を導入し、オゾン含有気泡5を生成するものであるので、排水1に含有された生物難分解性物質を生物処理可能な易分解性物質に分解することができる。   When the wastewater 1 is supplied to the decomposition tank 2, the decomposition tank 2 introduces ozone-added air 4 from the decomposition tank aeration pipe 3 and generates ozone-containing bubbles 5. Biodegradable substances can be decomposed into biodegradable easily degradable substances.

オゾン含有気泡5の気泡径は特に通常の膜分離活性汚泥法の範囲で良いが、生物難分解性物質との接触効率を向上するには数μm〜数mmであることが望ましい。   The bubble diameter of the ozone-containing bubbles 5 may be in the range of the ordinary membrane separation activated sludge method, but is preferably several μm to several mm in order to improve the contact efficiency with the biologically indegradable substance.

また、オゾン添加空気4のオゾン濃度は、分解槽2の上部空間で0.1ppmとなるような濃度とすることが望ましい。   The ozone concentration of the ozone-added air 4 is preferably set to a concentration of 0.1 ppm in the upper space of the decomposition tank 2.

排水1のTOC(全有機炭素濃度)が1000mg/Lのとき15ppm程度であれば生物難分解性物質を分解することができる。オゾンは排水1に溶解すると直に分解して消滅するため、分解水6への溶存はない。排水1のpHが酸性やアルカリ性域にある場合は、分解槽2で中性域にしておくことで後段の処理でpH調整をする必要がなく効率的である。   When the TOC (total organic carbon concentration) of the wastewater 1 is 1000 mg / L, the biodegradable substance can be decomposed if it is about 15 ppm. When ozone dissolves in the waste water 1, it decomposes and disappears directly, so there is no dissolution in the decomposed water 6. When the pH of the wastewater 1 is in the acidic or alkaline region, it is efficient by adjusting the pH in the subsequent treatment by making the decomposition tank 2 neutral.

次に、オゾンにより易分解性物質になった分解水6は、膜分離活性汚泥槽7に順次送られる。   Next, the decomposed water 6 that has become an easily decomposable substance by ozone is sequentially sent to the membrane separation activated sludge tank 7.

分解水6は、膜分離活性汚泥槽7で浮遊汚泥8に含まれる微生物により分解処理される。この分解過程で生物は排水1に含有される金属類を吸着還元することができる。   The decomposed water 6 is decomposed by microorganisms contained in the floating sludge 8 in the membrane separation activated sludge tank 7. In this decomposition process, the organism can adsorb and reduce the metals contained in the waste water 1.

膜分離活性汚泥槽7では、底部に設置された活性汚泥槽散気管9により、空気10が散気され好気性処理が行われる。空気10は活性汚泥槽散気管9により所定の大きさの気泡11となり、浸漬膜ユニット12中を上昇していく。気泡11は微生物の集合体からなる浮遊汚泥8の酸素供給源になるとともに、浸漬膜ユニット12表面への浮遊汚泥8の堆積を防止する働きを持っている。吸着や還元された金属類は、浮遊汚泥8の微生物に貯蓄されたり、微粒子となり浮遊汚泥8から排出され、分散したりする。   In the membrane separation activated sludge tank 7, air 10 is diffused by the activated sludge tank aeration pipe 9 installed at the bottom, and aerobic treatment is performed. The air 10 becomes bubbles 11 of a predetermined size by the activated sludge tank diffuser tube 9 and rises in the submerged membrane unit 12. The air bubbles 11 serve as an oxygen supply source of the floating sludge 8 made of an aggregate of microorganisms and have a function of preventing the accumulation of the floating sludge 8 on the surface of the submerged membrane unit 12. The adsorbed and reduced metals are stored in the microorganisms of the floating sludge 8 or discharged as fine particles from the floating sludge 8 and dispersed.

このとき、生物処理により析出した白金など金属微粒子は膜分離活性汚泥槽7で浮遊汚泥8と伴に分散している。   At this time, metal fine particles such as platinum deposited by biological treatment are dispersed together with the floating sludge 8 in the membrane separation activated sludge tank 7.

活性汚泥槽散気管9の鉛直上方に設置された浸漬膜ユニット12は、内部を吸引することにより、ろ過水13を排出する。浮遊汚泥8や析出した白金などの金属微粒子の粒径は数百nmから数μmであるが膜分離活性汚泥法で通常使用される膜の孔径は0.25μmから0.4μmであるため、膜分離活性汚泥槽7から排出されることは少なく、槽内で濃縮されていく。通常浮遊汚泥濃度として数万mg/L程度にまで濃縮することができる。   The submerged membrane unit 12 installed vertically above the activated sludge tank diffuser 9 discharges filtered water 13 by sucking the inside. Since the particle size of the metal particles such as the floating sludge 8 and precipitated platinum is several hundred nm to several μm, the pore diameter of the membrane usually used in the membrane separation activated sludge method is 0.25 μm to 0.4 μm. There is little discharge | emission from the separation activated sludge tank 7, and it concentrates in the tank. Usually, it can be concentrated to about tens of thousands mg / L as the suspended sludge concentration.

なお、処理工程を更に簡略したい場合は、分解槽2と膜分離活性汚泥槽7を共通化しても良い。共通化する場合は、オゾン添加空気4のオゾン濃度を浮遊汚泥8への影響がない濃度に変更する。変更する濃度は、膜分離活性汚泥槽7の上部空間でのオゾン濃度が0.1ppm以下となる様にすることが望ましい。   In order to further simplify the treatment process, the decomposition tank 2 and the membrane separation activated sludge tank 7 may be shared. In the case of common use, the ozone concentration of the ozone-added air 4 is changed to a concentration that does not affect the floating sludge 8. The concentration to be changed is preferably such that the ozone concentration in the upper space of the membrane separation activated sludge tank 7 is 0.1 ppm or less.

次に、濃縮水14は、膜分離活性汚泥槽7の底部から引抜かれ、沈降分離槽15に貯留される。そして濃縮水14を沈降汚泥16と上澄み液17に分離する。白金などの析出した金属微粒子は沈降せず分散し、上澄み液17に混入している。また、沈降分離槽15で沈降した沈降汚泥16にはまだ金属類が蓄積している生物がいるため、膜分離活性汚泥槽7へ返送する。この返送により、膜分離活性汚泥槽7の浮遊汚泥濃度を低下させることがなく、安定した処理が行える。   Next, the concentrated water 14 is extracted from the bottom of the membrane separation activated sludge tank 7 and stored in the sedimentation separation tank 15. The concentrated water 14 is separated into a settled sludge 16 and a supernatant liquid 17. Deposited metal fine particles such as platinum are dispersed without being settled and mixed in the supernatant liquid 17. In addition, since the sedimentation sludge 16 settled in the sedimentation separation tank 15 still has organisms in which metals are accumulated, it is returned to the membrane separation activated sludge tank 7. This return enables stable treatment without reducing the suspended sludge concentration in the membrane separation activated sludge tank 7.

また、生物が死滅して自己消化すると金属微粒子が回収でき効率が良い。一般的な活性汚泥の微生物は数日から数週間で世代交代し死滅すると言われるが、難分解性物質を分解したり、鉄を還元したりする特殊な微生物は世代交代期間が短く数時間から数十時間である。このため、金属を保有している生物が死滅し、自己消化するため金属微粒子が析出してしまうことになる。通常の膜分活性汚泥法では、増殖した微生物を余剰汚泥として排出してしまうが、この余剰汚泥の中にも金属類が含まれている可能性が高い。排水1に含まれる金属類が貴重で高価な白金等の貴金属である場合、汚泥は極力廃棄せず、白金を高純度で回収できればより効率がよい。   In addition, when the organism is killed and self-digested, the metal fine particles can be recovered and the efficiency is high. Generally, activated sludge microorganisms are said to change generations within a few days to weeks, and die. Dozens of hours. For this reason, the organisms holding the metal are killed and self-digested, so that the metal fine particles are deposited. In the normal membrane activated sludge method, the propagated microorganisms are discharged as surplus sludge. However, there is a high possibility that the surplus sludge contains metals. When the metals contained in the waste water 1 are precious metals such as precious and expensive platinum, sludge is not discarded as much as possible, and it is more efficient if platinum can be recovered with high purity.

沈降分離した上澄み液17は、更に分離部18に送水され、残処理水19と金属を含有したスラッジ20に分離される。分離部18は遠心分離装置や精密ろ過膜装置を用いることができる。残処理水19には分離できなかった金属類が残留している可能性があるため、更に膜分離活性汚泥槽7に返流し、金属微粒子となる処理を継続する。沈降汚泥16の返送と残処理水19の返流により、残留している金属類を金属微粒子とすることができ、回収率を向上することができる。金属類が白金など貴金属類の場合には、回収率が高いほどより有効である。ろ過水13に窒素など排水規制対象を含む場合には、それらの処理を実施することも容易である。   The supernatant liquid 17 that has settled and separated is further fed to a separation unit 18 where it is separated into residual treated water 19 and sludge 20 containing metal. The separation unit 18 can be a centrifuge or a microfiltration membrane device. Since there is a possibility that metals that could not be separated remain in the residual treated water 19, it is further returned to the membrane separation activated sludge tank 7 and the treatment to become metal fine particles is continued. By returning the settled sludge 16 and returning the residual treated water 19, the remaining metals can be made into metal fine particles, and the recovery rate can be improved. When the metals are noble metals such as platinum, the higher the recovery rate, the more effective. When the filtered water 13 includes drainage regulation targets such as nitrogen, it is easy to carry out these treatments.

分離部に遠心分離装置を用いた場合、比較的比重の重い金属を効率良く分離することができる。また、分離部に精密ろ過膜を用いた場合粒径が数nmの微細な粒子となる金属でも効率よく分離することができる。   When a centrifugal separator is used for the separation unit, a metal having a relatively high specific gravity can be efficiently separated. Further, when a microfiltration membrane is used for the separation part, even a metal that becomes a fine particle having a particle diameter of several nm can be efficiently separated.

このように、オゾン散気や沈降分離など簡単な処理工程を追加することにより、膜分離活性汚泥法でも容易に貴金属の回収が可能とすることができる。   In this way, by adding simple processing steps such as ozone aeration and sedimentation separation, it is possible to easily recover the noble metal even by the membrane separation activated sludge method.

従来は金属類を回収するための複雑な処理を実施する必要があったが、本発明によればオゾンと生物処理、分離装置を用いる簡単な回収工程により、金属類を容易に効率よく回収することができる。   Conventionally, it has been necessary to carry out complicated processing for recovering metals, but according to the present invention, metals are easily and efficiently recovered through simple recovery steps using ozone, biological treatment, and separation devices. be able to.

本発明にかかる排水処理装置は、オゾンと生物処理、分離装置で構成される簡単な処理で貴金属を回収することができ、微生物を利用していることから大変省エネルギーである。このため、本発明は、電子・自動車産業分野から上下水道、中水、井水など広範囲な水資源への展開が可能である。   The wastewater treatment apparatus according to the present invention can recover precious metals by a simple treatment composed of ozone, biological treatment, and separation equipment, and is very energy saving because it uses microorganisms. For this reason, the present invention can be applied to a wide range of water resources such as water and sewage, middle water, and well water from the electronic and automobile industries.

1 排水
2 分解槽
3 分解槽散気管
4 オゾン添加空気
5 オゾン含有気泡
6 分解水
7 膜分離活性汚泥槽
8 浮遊汚泥
9 活性汚泥槽散気管
10 空気
11 気泡
12 浸漬膜ユニット
13 ろ過水
14 濃縮水
15 沈降分離槽
16 沈降汚泥
17 上澄み液
18 分離部
19 残処理水
20 スラッジ
DESCRIPTION OF SYMBOLS 1 Wastewater 2 Decomposition tank 3 Decomposition tank aeration pipe 4 Ozone addition air 5 Ozone containing bubble 6 Decomposed water 7 Membrane separation activated sludge tank 8 Floating sludge 9 Activated sludge tank aeration pipe 10 Air 11 Bubble 12 Immersion membrane unit 13 Filtration water 14 Concentrated water 15 Sedimentation separation tank 16 Sedimentation sludge 17 Supernatant liquid 18 Separation part 19 Residual treated water 20 Sludge

Claims (6)

オゾン添加空気により金属を含有する生物難分解性排水を分解して分解水を得る分解槽と、微生物により前記分解水から金属を微粒子として還元して金属含有汚泥を含む濃縮水を得る膜分離活性汚泥層と、前記濃縮水中の汚泥を沈降させて上澄み液を得る沈降分離槽とで、分離部により前記上澄み液から金属を回収する固液分離装置を備えることを特徴とする排水処理装置。 Decomposition tank for decomposing biodegradable wastewater containing metals with ozone-added air to obtain decomposed water, and membrane separation activity for obtaining concentrated water containing metal-containing sludge by reducing metals from the decomposed water as fine particles by microorganisms A wastewater treatment apparatus, comprising: a sludge layer; and a sedimentation tank for collecting a sludge in the concentrated water to obtain a supernatant, and a solid-liquid separator for recovering metal from the supernatant by a separation unit. 沈降分離槽で沈降した汚泥を膜分離活性汚泥槽へ戻すことを特徴とする、請求項1記載の排水処理装置。 The wastewater treatment apparatus according to claim 1, wherein sludge settled in the settling separation tank is returned to the membrane separation activated sludge tank. 固液分離槽で金属が回収された残処理水を膜分離活性汚泥槽へ戻すことを特徴とする、請求項1記載の排水処理装置。 The wastewater treatment apparatus according to claim 1, wherein the residual treated water from which the metal has been recovered in the solid-liquid separation tank is returned to the membrane separation activated sludge tank. 分離部に遠心分離装置を用いることを特徴とする、請求項1または3記載の排水処理装置。 The wastewater treatment apparatus according to claim 1 or 3, wherein a centrifugal separator is used for the separation unit. 分離部に精密ろ過膜を用いることを特徴とする、請求項1または3記載の排水処理装置。 The wastewater treatment apparatus according to claim 1 or 3, wherein a microfiltration membrane is used for the separation part. 分離部に用いる精密ろ過膜の孔径が0.4μm以下であることを特徴とする、請求項5記載の排水処理装置。 6. The waste water treatment apparatus according to claim 5, wherein the pore size of the microfiltration membrane used for the separation part is 0.4 μm or less.
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