JPS60190290A - Treatment of organic waste water - Google Patents

Treatment of organic waste water

Info

Publication number
JPS60190290A
JPS60190290A JP4643384A JP4643384A JPS60190290A JP S60190290 A JPS60190290 A JP S60190290A JP 4643384 A JP4643384 A JP 4643384A JP 4643384 A JP4643384 A JP 4643384A JP S60190290 A JPS60190290 A JP S60190290A
Authority
JP
Japan
Prior art keywords
waste water
manganese dioxide
cod
phosphorus
nitrogen
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.)
Pending
Application number
JP4643384A
Other languages
Japanese (ja)
Inventor
Noriyuki Imada
今田 宣之
Toshiteru Okada
岡田 敏照
Kazuhide Miyazaki
宮崎 和英
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsui Mining and Smelting Co Ltd
Original Assignee
Mitsui Mining and Smelting Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Mitsui Mining and Smelting Co Ltd filed Critical Mitsui Mining and Smelting Co Ltd
Priority to JP4643384A priority Critical patent/JPS60190290A/en
Publication of JPS60190290A publication Critical patent/JPS60190290A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To remove nitrogen and chromaticity at a stroke, by applying manganese dioxide treatment to waste water containing an org. substance and having pH adjusted to 5 or more to reduce COD, phosphorus, nitrogen and chromaticity. CONSTITUTION:In treating waste water containing an org. substance and high in content of COD, phosphorus and ammonia such as urban sewage, excretion waste water or factory waste water, alkali is added to waste water to adjust the pH thereof to 5 or more because there is possibility such that Mn<2+> is eluted when waste water is acidic. Next, this waste water is passed through a packed cylinder packed with a manganese dioxide filter material to perform adsorption and oxidative decomposition of the org. substance, phosphorus and nitrogen. With respect to waste water high in COD concn., a packed cylinder packed with the manganese dioxide filter material is used in a multi-stage fashion to make it possible to obtain treated water low in COD concn.

Description

【発明の詳細な説明】 本発明は有機性1ノド水の処理方法に関し、詳しくは都
市下水、尿尿排水、工場排水等に含まれるイ1機性物質
を二酸化マンガンを用いて吸着および酸化分解−する0
機性排水の処理方法に関り゛るものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating organic water, and more specifically, it involves adsorption and oxidative decomposition of organic substances contained in urban sewage, urine wastewater, industrial wastewater, etc. using manganese dioxide. -0 to do
This relates to a method for treating mechanical wastewater.

近年、湖沼等の開鎖水域への流入水の水質は″rUS栄
養化の面から窒素、リン等の1度規制が強化されてきて
おり、また有機性物質に起因づ−る化学的酸素要求1n
(COD)も高度に処理することが要求され又いる。
In recent years, the quality of water flowing into open water bodies such as lakes and marshes has been strengthened with respect to nitrogen, phosphorus, etc., from the perspective of ``rUS nutrition,'' and chemical oxygen demand caused by organic substances has been strengthened.
(COD) is also required to be processed at a high level.

従来より有機性物質を含有する抽水の処理としては、一
般に生物的処理、すなわち活性汚泥法が処理コストが安
いことから広く用いられているが、この方法では高濃度
のCODをio ppm以下の濃度に処理することが困
難であり、また生物難分解性物質に起因するCODに対
してはほとんど効果を有していないのが現状である。
Conventionally, biological treatment, namely the activated sludge method, has been widely used to treat extracted water containing organic substances due to its low processing cost. Currently, it is difficult to treat COD caused by biorefractory substances, and it has almost no effect on COD caused by biorefractory substances.

このため、高濃度の有機性物質含有排水には、さらに高
度処理をする必要があり、活性炭吸着法および塩素やオ
ゾンによる酸化処理の併用が必要である。
For this reason, wastewater containing high concentrations of organic substances requires further advanced treatment, and requires the combined use of activated carbon adsorption and oxidation treatment using chlorine or ozone.

しかしながら、活性炭吸着法では生物難分解性物質が一
般に高分子化合物であるため、活性炭中の細孔(数10
〜数100人)への吸着、拡散が悪く、活性炭の寿命が
短いという欠点がある。
However, in the activated carbon adsorption method, since the biologically persistent substances are generally polymeric compounds, the pores in the activated carbon (several tens of
Activated carbon has the drawbacks of poor adsorption and diffusion, and short lifespan of activated carbon.

塩素またはオゾン酸化法は、設備費および処理コストが
高いため特殊な場合以外は広く利用されていない。
Chlorine or ozone oxidation methods are not widely used except in special cases because of high equipment costs and processing costs.

−fj、リン含有排水の処理法としては、凝東沈澱法が
一般的であるが、この方法では処理によって発生層る汚
泥が濃縮性や脱水性が悪いため、汚泥処理が困難である
という問題がある。
- fj, the common method for treating phosphorus-containing wastewater is the coagulation sedimentation method, but this method has the problem that sludge treatment is difficult because the sludge that forms during treatment has poor thickening and dewatering properties. There is.

さらに、排水中のアンモニア性窒素の処理方法′として
は、従来よりアンモニアストリッピング法、生物処理法
a3よびゼオライトによる吸着法が知られている。
Furthermore, as methods for treating ammonia nitrogen in wastewater, ammonia stripping method, biological treatment method a3, and adsorption method using zeolite are conventionally known.

これらのいずれの処理方法においても、COO。In any of these treatment methods, COO.

リン、窒素および色度を同時に低減さぜることはほどん
ど不可能であった。
It was almost impossible to reduce phosphorus, nitrogen and color at the same time.

本発明は、かかる要求に基づきなされたもので、排水中
のCOO,リン、窒素および色度を一挙に除去する有機
性排水の処理方法を提供することを目的とする。
The present invention was made based on such requirements, and an object of the present invention is to provide a method for treating organic wastewater that removes COO, phosphorus, nitrogen, and chromaticity in wastewater all at once.

水弁111j者らは、この目的に従って、種々研究の結
果、排水中に二酸化マンガンを添加することによって、
排水中のCOD、リン、窒素および色度を吸着および酸
化分解し、−挙に除去することを見い出し本発明に至っ
たものである。
In accordance with this purpose, as a result of various studies, water valve 111j people have found that by adding manganese dioxide to wastewater,
The present invention was based on the discovery that COD, phosphorus, nitrogen, and chromaticity in wastewater can be adsorbed, oxidized and decomposed, and removed all at once.

すなわら本発明は、有機性物質を含イイする排水の処理
においで、二酸化マンガンを用いることによって、CO
D、リン、窒素および色度を低減させることを特徴とす
る有機性排水の処理方法にある。
In other words, the present invention uses manganese dioxide to reduce CO2 in the treatment of wastewater containing organic substances.
D. A method for treating organic wastewater characterized by reducing phosphorus, nitrogen and chromaticity.

このように本発明においては、有機性排水中の生物難分
解性物質等を二酸化マンガンを用いて酸化分解さIるこ
とにより、排水中のCODならびに色度を効果的に除去
すると同時に、排水中のリンおよびアンモニア性窒素を
吸着させるという効果を有づる処理方法である。
In this way, in the present invention, by oxidizing and decomposing non-biodegradable substances, etc. in organic wastewater using manganese dioxide, COD and chromaticity in wastewater can be effectively removed, and at the same time, COD in wastewater can be effectively removed. This treatment method has the effect of adsorbing phosphorus and ammonia nitrogen.

以下、本発明の処理り法について説明する。The processing method of the present invention will be explained below.

本発明にJJいC処理の対乍となるJJI水は、都市下
水、原体排水、■揚排水等の有機性物質を含有づるCO
Dやリン、アン七ニノノ含有ωが高い排水ぐある。
JJI water, which is the counterpart of JJC treatment in the present invention, is CO water containing organic substances such as urban sewage, raw wastewater, and pumped wastewater.
There is drainage water that is high in D, phosphorus, and oxidant content.

これらの排水を処理するためには、排水中の1)11が
4以下の酸性排水の場合は微量のMllが溶出り−る恐
れがあるため、アルカリを加えてpl−1を5以上にす
る中和工程を予め採用することが必要である。
In order to treat these wastewaters, 1) If the wastewater is acidic with 11 being 4 or less, a trace amount of Mll may be eluted, so alkali is added to increase the pl-1 to 5 or more. It is necessary to employ a neutralization step beforehand.

次に、pi−15以上に中和された排水は、二酸化マン
ガン浦材を充填した充填筒に通水され、有機性物質、リ
ンおにび窒素を吸着、酸化分解さける。
Next, the wastewater neutralized to pi-15 or higher is passed through a cylinder filled with manganese dioxide material to adsorb and oxidize organic substances, phosphorus, and nitrogen, and to avoid oxidative decomposition.

CoDilfl度の高いJJ)水については、二酸化マ
ンガン’dM Ulを充填した充161問を多段で使用
することによりCoDl度の低い処理水を得ることが出
来るが、活性汚泥法を前工程に設置し、予めCOD濃度
を100 ppm以下に低減させておくことにより、二
酸化マンガンill +AのスI命を長くJ−ることが
できる。また、色度については、例えば尿尿中に含有さ
れる胆汁色素は、活性汚泥法では除去が不充分であるが
、本発明による処理方法では二酸化マンガン1Iil材
を通過させるだけで透明に近い処理水が得られる。
For JJ) water with a high CoDil content, treated water with a low CoDil content can be obtained by using multiple stages of water filled with manganese dioxide'dM Ul, but it is possible to obtain treated water with a low CoDil content. By reducing the COD concentration to 100 ppm or less in advance, the life of manganese dioxide ill +A can be extended. Regarding chromaticity, for example, bile pigments contained in urine cannot be removed sufficiently by the activated sludge method, but with the treatment method of the present invention, the color can be almost transparent by simply passing through the manganese dioxide 1Iil material. water is available.

本発明で用いられる二酸化マンガンは、適当な通水速度
をもたせるため、粒状であることが必要である。粒状二
酸化マンガンをiqるためには各種の方法が考えられる
が、例えば二酸化マンガンの結晶が移転覆る際、粒子同
士が固結覆る現象を応用して粒状化させたものが使用で
きる。このような粒状二酸化マンガンは表面観察の結果
、マクロ的にポーラスでしかも表面に1μ以下の針状結
晶が照故に存在しており、このことが生物難分解性物質
の酸化J3よびリン、窒素の吸着に対し、非常に有効な
ものと思われる。
The manganese dioxide used in the present invention needs to be granular in order to provide an appropriate water flow rate. Various methods can be used to iq granular manganese dioxide, but for example, one that is granulated by applying the phenomenon in which particles solidify and cover each other when manganese dioxide crystals transfer and cover can be used. As a result of surface observation of such granular manganese dioxide, it was found that it is macroscopically porous and needle-like crystals of less than 1 μm exist on the surface due to illumination. It seems to be very effective against adsorption.

本発明の処理方法は、以上の工程からなり、従来より提
案、実施されている処理方法と比較し、非常に簡単でし
かも高効率を有する処理方法である。
The treatment method of the present invention consists of the above-mentioned steps, and is a treatment method that is extremely simple and highly efficient compared to treatment methods that have been proposed and implemented in the past.

以下、実施例によってさらに詳細に本発明を説明りるが
、本発明はこの実施例によって限定されるしのではない
EXAMPLES Hereinafter, the present invention will be explained in more detail with reference to Examples, but the present invention is not limited to these Examples.

実 施 例 1 0.4〜0.6#の粒状二酸化マンガン100ccをガ
ラス製円筒に充填し、この円筒上部よりCOD淵度81
 pHlllの尺体消化脱離液を、SV比が1〜51/
1−1rの速度で通水した。
Example 1 100 cc of granular manganese dioxide of 0.4 to 0.6# was filled into a glass cylinder, and a COD depth of 81 was poured from the top of the cylinder.
The pHllll ulnar digestion and desorption fluid was prepared with an SV ratio of 1 to 51/
Water was passed through at a rate of 1-1r.

通水後のCOD濃度を第1図に示す。Figure 1 shows the COD concentration after water flow.

第1図に示されるように処理水のCoDil度は約25
〜35 ppmとなりCOD除去率は約65%であった
。また実施したSV比の範囲では処理水のCOD濃度に
大きなZG 4よ見られなかった。
As shown in Figure 1, the CoDil degree of the treated water is approximately 25.
~35 ppm, and the COD removal rate was approximately 65%. Furthermore, within the range of SV ratios tested, no large COD concentration was observed in the treated water compared to ZG4.

色度については床体消化脱離液は濃い黄色味をJ3びC
いるが、処理水の色は透明に近いうずい黄色どなった。
In terms of chromaticity, the bed body digestion and desorption fluid has a deep yellowish color of J3 and C.
However, the color of the treated water was a dull yellow, almost transparent.

また、1京水中のリンJ3よび窒素の1liIUはそれ
ぞt’L 15 ppmト1351111m テlr 
ッだ(1) 1.:対し、SV比を1で通水した処理水
のilJ度は、それぞれ0.2 ppmと7.3111
110に低減した。
In addition, 1liIU of phosphorus J3 and nitrogen in 1 quintillion water are t'L 15 ppm and 1351111m telr, respectively.
dda (1) 1. : On the other hand, the ilJ degree of treated water passed through with an SV ratio of 1 is 0.2 ppm and 7.3111, respectively.
It was reduced to 110.

火−」L−Am」し 圧体消化11(2因1液を水道水で4イ8に希釈してC
ODm度20 pp+n、リン濃度4.Q ppmおよ
びアンモニア性窒素濃度34 ppmとしたものを試料
液とし、実施例1ど同様な方法によりSV比を1の速度
で通水した。
Tue-"L-Am" and pressurized body extinguishing 11 (2 parts 1 liquid diluted to 4 to 8 with tap water and C
ODm degree 20 pp+n, phosphorus concentration 4. Q ppm and an ammonia nitrogen concentration of 34 ppm were used as sample solutions, and water was passed through the sample solution at a speed of SV ratio 1 in the same manner as in Example 1.

処理水のCOD’a度は7.0 ppm、リン濃度0.
0ppmおよびアンモニア性窒素濃度は4.、Oppm
に低下し色度も711を色透明になった。
The COD'a degree of the treated water is 7.0 ppm, and the phosphorus concentration is 0.
0 ppm and ammonia nitrogen concentration is 4. , Oppm
The chromaticity decreased to 711 and the color became transparent.

以上説明した如く、二酸化マンガンを用いた本発明の処
理I)法は、有機性物質を含有する排水のCOD、リン
、窒素および色度の除去に非常に有効であり、CoDI
a度が1100pp程度の排水に対しては本発明による
二酸化マンガン充填塔を2〜3す用いれば充分である。
As explained above, the treatment method I) of the present invention using manganese dioxide is very effective in removing COD, phosphorus, nitrogen and chromaticity from wastewater containing organic substances, and CoDI
For wastewater with a degree of about 1100 pp, it is sufficient to use two to three manganese dioxide packed towers according to the present invention.

このように本発明による処理方法は、数種の物質を間開
に除去出来、またプロセス自体が非常に簡便なため、設
備費も安くて済むという利点も右していることから、有
機性排水の処理方法として好適に用いられる。
In this way, the treatment method according to the present invention can remove several types of substances at intervals, and the process itself is very simple, so equipment costs are low. It is suitably used as a treatment method.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は通水速度(SV比)と処理水のCOD濃度との
関係を示すグラフである。 特a’F出W1人 三井金属鉱業株式会社代理人 弁理
士 伊東辰雄 代理人 弁理士 伊束哲出 病へ 1 え”、虚 1 2 3 4 5 通水達度sv比u/Hrt
FIG. 1 is a graph showing the relationship between water flow rate (SV ratio) and COD concentration of treated water. Special a'F exit W1 person Mitsui Kinzoku Mining Co., Ltd. agent Patent attorney Tatsuo Ito agent Patent attorney Tetsuo Izuka's disease 1 E'', Imaginary 1 2 3 4 5 Water flow rate sv ratio u/Hrt

Claims (1)

【特許請求の範囲】 J3よび色度を低減さゼることを特徴とする有機性排水
の処理方法。 2、前記二酸化マンガン処理前の排水がIl+−15以
上に中和処理される前記特許請求の範囲第1項に記載の
有機11排水の処理方法。 3、前記二酸化マンガンが粒状でマクロ的にポーラスで
ある前記特許請求の範囲第1項または第2項記載の有機
性排水の処理方法。 4、前記二酸化マンガンが充填筒に充填されているOr
J記特許請求の範囲第1項、第2項または第3項に記載
の右IMtI JJI水の処理方法。 5、前記充填筒が多段である前記特許請求の範囲第4項
記載の有機性排水の処理方法。
[Claims] A method for treating organic wastewater, characterized by reducing J3 and chromaticity. 2. The method for treating organic 11 wastewater according to claim 1, wherein the wastewater before the manganese dioxide treatment is neutralized to Il+-15 or higher. 3. The method for treating organic wastewater according to claim 1 or 2, wherein the manganese dioxide is granular and macroscopically porous. 4. Or in which the manganese dioxide is filled in the filling cylinder
A method for treating IMtI JJI water as set forth in Claims 1, 2, or 3. 5. The method for treating organic wastewater according to claim 4, wherein the filling cylinder has multiple stages.
JP4643384A 1984-03-13 1984-03-13 Treatment of organic waste water Pending JPS60190290A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4643384A JPS60190290A (en) 1984-03-13 1984-03-13 Treatment of organic waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4643384A JPS60190290A (en) 1984-03-13 1984-03-13 Treatment of organic waste water

Publications (1)

Publication Number Publication Date
JPS60190290A true JPS60190290A (en) 1985-09-27

Family

ID=12747015

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4643384A Pending JPS60190290A (en) 1984-03-13 1984-03-13 Treatment of organic waste water

Country Status (1)

Country Link
JP (1) JPS60190290A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005305266A (en) * 2004-04-20 2005-11-04 Victor Co Of Japan Ltd Treatment method and treatment apparatus for organic waste water
WO2010115810A1 (en) * 2009-04-09 2010-10-14 Wieland Dental + Technik Gmbh & Co. Kg Method for treating waste materials containing nitrite
JP6232606B1 (en) * 2017-04-27 2017-11-22 株式会社ノアテック Wastewater treatment method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5684688A (en) * 1979-12-12 1981-07-10 Nojimagumi:Kk Terminal treatment of waste water
JPS58137492A (en) * 1982-02-10 1983-08-15 Suido Kiko Kk Method for removing color of water
JPS5936592A (en) * 1982-08-23 1984-02-28 Sekisui Enbairomento:Kk Treatment of sewage

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5684688A (en) * 1979-12-12 1981-07-10 Nojimagumi:Kk Terminal treatment of waste water
JPS58137492A (en) * 1982-02-10 1983-08-15 Suido Kiko Kk Method for removing color of water
JPS5936592A (en) * 1982-08-23 1984-02-28 Sekisui Enbairomento:Kk Treatment of sewage

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005305266A (en) * 2004-04-20 2005-11-04 Victor Co Of Japan Ltd Treatment method and treatment apparatus for organic waste water
JP4617099B2 (en) * 2004-04-20 2011-01-19 株式会社メイコー Organic wastewater treatment method and treatment apparatus
WO2010115810A1 (en) * 2009-04-09 2010-10-14 Wieland Dental + Technik Gmbh & Co. Kg Method for treating waste materials containing nitrite
JP6232606B1 (en) * 2017-04-27 2017-11-22 株式会社ノアテック Wastewater treatment method

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