JPH04193387A - Method for purifying sewage - Google Patents

Method for purifying sewage

Info

Publication number
JPH04193387A
JPH04193387A JP32643390A JP32643390A JPH04193387A JP H04193387 A JPH04193387 A JP H04193387A JP 32643390 A JP32643390 A JP 32643390A JP 32643390 A JP32643390 A JP 32643390A JP H04193387 A JPH04193387 A JP H04193387A
Authority
JP
Japan
Prior art keywords
sewage
contact
grains
bringing
wastewater
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
JP32643390A
Other languages
Japanese (ja)
Inventor
Mitsuo Maeyama
前山 光雄
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.)
MAEYAMA KK
Mitsui and Co Ltd
Original Assignee
MAEYAMA KK
Mitsui and 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 MAEYAMA KK, Mitsui and Co Ltd filed Critical MAEYAMA KK
Priority to JP32643390A priority Critical patent/JPH04193387A/en
Publication of JPH04193387A publication Critical patent/JPH04193387A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To purify all kinds of sewage by utilizing the material existing in the natural world by bringing the sewage into contact with red balls formed by granulating clay contg. aluminum silicate and bringing the sewage into contact with magnetite ore grains. CONSTITUTION:The sewage emitted from an original liquid prepn. tank is introduced into a primary treating tank B where the sewage is brought into contact with the red balls 5 formed by granulating the clay contg. the aluminum silicate while the sewage is kept stirred by injection of air. The smells of the sewage are adsorbed into the red balls 5 and secondary mineral materials are migrated into primary mineral materials. The sewage emitted from the primary treating tank B is introduced to a secondary treating layer C where the sewage passes the red balls 5, magnetite ore grains 9, limestone grains 10, hydrous silicate 11 of zeolite, etc., red balls 5, limestone grains 10, quartz grains 12, and red balls 5 packed in containers 8a to 8h. The secondary mineral ores are migrated into the primary mineral ores at this time and the stabilization of the magnetic fields in the sewage, the purification by the limestone grains 10, the elution of mineral-components by the hydrous silicate 11, etc., are executed at this time.

Description

【発明の詳細な説明】 産業上の利用分野 本発明は、工場等で排出きれる現像液、メツキ液、パル
プ廃液、またゴルフ場などから排出きれる農薬を含んだ
排水等の様々な有害産業廃液及び汚れた湖沼等の水を処
理し、浄化(無害化)するための天然物を利用した汚水
処理システムに関するものである。
DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application The present invention is applicable to various harmful industrial waste liquids such as developer solution, plating solution, pulp waste liquid discharged from factories, etc., and wastewater containing pesticides discharged from golf courses, etc. This relates to a sewage treatment system that uses natural products to treat and purify (detoxify) polluted water from lakes and marshes.

工場等から排出される産業廃液等には、一般に有機物等
の有害物質を含んでいるが、その種類は多種多様であり
、従来から様々な方法により処理されている。
BACKGROUND OF THE INVENTION Industrial waste fluid discharged from factories and the like generally contains harmful substances such as organic substances, which come in a wide variety of types and have been treated using various methods.

これら有機物の浄化状態の測定基準として、生物化学的
酸素要求量(BOD)、化学的酸素要求量(COD)等
がある。
Biochemical oxygen demand (BOD), chemical oxygen demand (COD), etc. are used as standards for measuring the purification state of these organic substances.

自然界の水は、それ自体に自浄能力を有しており、バラ
ンスがとれている。この要因の一つに、磁場の作用があ
るといわれており、汚水等では磁場のバランスが崩れて
いるために、浄化作用を発揮出来ないでいる。
Water in nature has its own self-purifying ability and is well balanced. One of the reasons for this is said to be the effect of the magnetic field, and in sewage, etc., the magnetic field is unbalanced, so it is unable to exert its purifying effect.

従  来  技  術 一般【こ無機の懸濁質を含む廃液の処理には、自然沈降
により分離する沈降分離法や、自然沈降しない極微細な
粒子などの除去のために凝集剤を添加して分離させる凝
集分離法や、フロックや懸濁物質か軽くまた疎水性の場
合は、気泡を付着菌せて浮上分離する加圧又は電解浮上
法等が採用きれ、廃液に有機物質を含んでいる場合には
、微生物を用いて有機物を分解する活性汚泥法等の処理
方法が採用きれているが、特に廃液に懸濁液を多く含む
場合、pH異常の場合、許客値以上の有害物質が含まれ
ている場合、フェノール、アルデヒド、ケトン類が含ま
れる場合及び重金属イオンやシアンが含まれる場合停は
、前処理など多次に亘る処理過程を必要とする。
Conventional technology in general [To treat wastewater containing inorganic suspended solids, there are two methods: a sedimentation separation method that separates by natural sedimentation, and a separation method by adding a flocculant to remove ultrafine particles that do not naturally settle. If the flocs or suspended matter are light and hydrophobic, pressure or electrolytic flotation methods can be used to float and separate the bacteria by attaching air bubbles, and if the waste liquid contains organic substances, Treatment methods such as the activated sludge method, which uses microorganisms to decompose organic matter, have been successfully adopted for wastewater treatment, but especially when the wastewater contains a large amount of suspended liquid or has an abnormal pH, it may contain harmful substances exceeding the permissible value. In cases where phenol, aldehydes, ketones, or heavy metal ions or cyanide are included, multiple treatment steps such as pretreatment are required.

発明が解決しようとする課題 その為有機性でBODやCODの高い廃液の場合は特別
の処理を必要とする為に廃液の処理に時間と多額のコス
トがかかるために海洋投棄や地中埋設等の処置が行なわ
れているが、最近ではかかる投棄や埋設のために二次公
害が発生し、河川、湖沼、地下水の水質が劣化し、奥書
や大気汚染。
Problems to be Solved by the Invention Therefore, in the case of organic waste liquid with high BOD and COD, special treatment is required, which takes time and a large amount of cost, so it is difficult to dispose of it in the ocean or bury it underground. However, recently secondary pollution has occurred due to such dumping and burial, and the water quality of rivers, lakes, and groundwater has deteriorated, and air pollution has occurred.

土壌汚染等の環境破壊が進み、地球上の生物、物質に悪
影響を与えている。
Environmental destruction such as soil pollution is progressing, and it is having a negative impact on living things and materials on earth.

そこで本発明はかかる、従来技術の欠点に鑑みなされた
もので、薬品類を使用することなくBODやCODの値
を下げることができると共に重金属イオンの除去を行な
うことのできる廃液処理システムを提供することを目的
とする。
The present invention was made in view of the drawbacks of the prior art, and provides a waste liquid treatment system that can lower BOD and COD values and remove heavy metal ions without using chemicals. The purpose is to

問題点を解決するための手段 すなわち汚水をアルミノ硅酸塩を含有した粘土を造粒し
てなる赤玉と接触させる工程と、汚水を磁鉄鉱石粒と接
触させる工程とからなる汚水の浄化方法により本目的を
達成する。尚各工程の反応を促進する意味において、空
気を汚水中に噴出させながら空気攪拌を行なうと良い。
In order to solve this problem, we developed a method for purifying sewage that consists of the steps of bringing the sewage into contact with Akadama, which is made by granulating clay containing aluminosilicate, and bringing the sewage into contact with magnetite grains. Achieve your purpose. In order to promote the reactions in each step, it is preferable to perform air agitation while blowing air into the waste water.

次に汚水が有機物質を多量に含む場合には、汚水をアル
ミノ硅酸塩を含有した粘土を造粒してなる赤玉と接触さ
せる工程と、汚水を磁鉄鉱石粒と接触させる工程と、汚
水を鉄又はアルミニウム金属と接触させる工程と、汚水
をゼオライト等の含水硅酸塩と接触させる工程と、汚水
を石灰石等の炭酸力ルンウムと接触させる工程とからな
る汚水の浄化方法により汚水を浄化する。尚この場合も
各工程の反応を促進する意味において、空気を汚水中に
噴出させながら空気攪拌を行なうと良い。
Next, when the sewage contains a large amount of organic substances, a step of bringing the sewage into contact with red beads made by granulating clay containing aluminosilicate, a step of bringing the sewage into contact with magnetite ore grains, and a step of bringing the sewage into contact with magnetite grains. Sewage is purified by a method for purifying sewage comprising the steps of bringing the sewage into contact with iron or aluminum metal, contacting the sewage with a hydrous silicate such as zeolite, and contacting the sewage with a carbonate such as limestone. In this case as well, in order to promote the reactions in each step, it is preferable to perform air agitation while blowing air into the waste water.

接触させる赤玉等の粒の粒径は、0.5〜5.0wn程
度のものが好ましい。
The grain size of the grains to be contacted, such as red balls, is preferably about 0.5 to 5.0 wn.

作     用 アルミノ硅酸塩を含む赤玉を処理水とを接触させること
により、廃液中に含まれる2次鉱物質(例えは第二鉄イ
オン)を1次鉱物質(第一鉄イオン)に移行させる。
Action: By bringing Akadama containing aluminosilicate into contact with treated water, secondary minerals (e.g. ferric ions) contained in the waste liquid are transferred to primary minerals (ferrous ions). .

磁鉄鉱石粒Fa”(Fe”Fa”)04を処理水と接触
させることにフェリ磁性等の作用により汚水中の墓場の
乱れを正し、安定化させる。
By bringing the magnetite grains Fa"(Fe"Fa") 04 into contact with the treated water, the turbulence in the wastewater is corrected and stabilized due to the action of ferrimagnetism.

鉄又はアルミニウム金属と汚水とを接触させることによ
り、イオン化傾向の小きい金属(Zn、Cr、 Cd、
 Co、 Ni、 Sn、 Pb、 Cu−)等を析出
させる・ゼオライト等の含水硅酸塩と汚水とを接触させ
ることにより、汚水中にミネラル成分であるHg、に等
を溶出させ、水を活性化する。
By bringing iron or aluminum metal into contact with wastewater, metals with a low ionization tendency (Zn, Cr, Cd,
Co, Ni, Sn, Pb, Cu-), etc. are precipitated. By bringing water-containing silicates such as zeolite into contact with wastewater, mineral components such as Hg, etc. are eluted in the wastewater, and the water is activated. become

汚水を石灰石等の炭酸カルンウムと接触させることによ
り水のpHを7〜8にllI!すると共に、炭酸カルシ
ウムのもつ水の浄化作用によりきらに水を浄化する。
By bringing the wastewater into contact with carunium carbonate such as limestone, the pH of the water can be adjusted to 7-8! At the same time, the water purification effect of calcium carbonate also purifies the water.

汚水中での各物質との接触過程において汚水中に空気を
噴出させ、攪拌することにより物質と水との接触回数が
増加し、反応時間を短縮化させることができる。
By blowing air into the wastewater and stirring it during the contact process with each substance in the wastewater, the number of times the substances come into contact with water can be increased and the reaction time can be shortened.

また空気中の酸素が、汚水中に溶は込むことにより、汚
水を活性化させると共に懸濁物質の沈降性を高めること
ができる。
Furthermore, by dissolving oxygen in the air into the wastewater, it is possible to activate the wastewater and improve the settling properties of suspended solids.

実  施  例 以下に本発明を図面に示きれた実施例に従って詳細に説
明する。
Embodiments The present invention will be explained in detail below according to embodiments shown in the drawings.

実施例−1 汚水の処理槽として、原液調整槽A、1次処理槽B、2
次処理檀C13次処理槽り、4次処理槽Eを用いる。 
原液処理槽Aは第2図に示すように、槽Aの底部に空気
配管1を施してあり、該空気配管1から汚水中に空気を
噴出するように構成されており、2は汚水の供給口、3
は汚水の処理水の排出口である。
Example-1 Raw solution adjustment tank A, primary treatment tank B, 2 as wastewater treatment tanks
Next treatment tank C1 3rd treatment tank and 4th treatment tank E are used.
As shown in Fig. 2, the raw solution treatment tank A is equipped with an air pipe 1 at the bottom of the tank A, and is configured to blow air into the wastewater from the air pipe 1. mouth, 3
is the outlet for treated wastewater.

この排出口3は1次処理槽Bと連通しており、1次処理
槽Bは、第3図に示すようにその底部に空気配管4が施
してあり、該配管4から汚水中に空気が1出するように
構成きれており、汚水の表面部には、アルミ。ノ硅酸塩
を含有する粘土(山梨県産)を造粒した赤玉(1〜5m
)5がメツシュ又はパンチングされた容器6に充填され
ている。
This discharge port 3 communicates with the primary treatment tank B, and the primary treatment tank B has an air pipe 4 provided at its bottom as shown in FIG. 1.The surface of the wastewater is made of aluminum. Akadama (1 to 5 m
) 5 is filled into a mesh or punched container 6.

尚、1次処理槽単独を浄化槽として使用する場合には、
赤玉の代わりに赤玉60%9石灰石30%及び磁鉄鉱石
10%をそれぞれ造粒したもの、又は赤玉85%及び磁
鉄鉱石15%をそれぞれ造粒したものを用いる。
In addition, when using the primary treatment tank alone as a septic tank,
Instead of Akadama, granules of 60% Akadama, 30% limestone, and 10% magnetite ore, or granules of 85% Akadama and 15% magnetite ore, are used.

接触後の水は、配管7を介して2次処理槽Cに導かれる
The water after contact is led to the secondary treatment tank C via the pipe 7.

二次処理槽Cは、第4図に示すように5田程度の孔が複
数パンチングされた8つの容器8a、8b。
As shown in FIG. 4, the secondary treatment tank C consists of eight containers 8a and 8b each having a plurality of holes punched therein.

8c、 8d、 8e、 8f、 8g、 8hにより
9つに区画されており、該容器8内にはそれぞれ、赤玉
5、磁鉄鉱石粒92石灰石粒10.沸石等の含水硅酸塩
11.赤玉52石灰石粒10、石英粒12.赤玉5が詰
め込まれている。
It is divided into nine sections by 8c, 8d, 8e, 8f, 8g, and 8h, and inside the container 8 are 5 red balls, 92 magnetite grains, 10 limestone grains, and 10. Hydrous silicates such as zeolite 11. 52 red balls, 10 limestone grains, 12 quartz grains. It is packed with 5 red balls.

2次処理槽Cの排出管13は3次処理槽りと連通してい
る。3次処理槽りは第5図に示すように仕切板14a、
 14b、 15a、 15b、 L6a、 16b、
 1ea、 17b。
The discharge pipe 13 of the secondary treatment tank C communicates with the tertiary treatment tank. As shown in FIG. 5, the tertiary treatment tank has partition plates 14a,
14b, 15a, 15b, L6a, 16b,
1ea, 17b.

18a 、 18b 、 19a 、 19bを介して
7つに区画されており、該区画きれた檜の底部には空気
配管20 、21 。
It is divided into seven sections via 18a, 18b, 19a, and 19b, and air pipes 20, 21 are installed at the bottom of the sectioned cypress.

22、23.24.25.26が設置きれ、汚水中に空
気を噴出するように構成きれている。仕切板14a、1
4b、仕切板15m 、 15b 、仕切板16a、1
6b、仕切板17a、17b、仕切板18a 、 18
b 、及び仕切板19a、19b間は所定の空間隔てて
設置されており、仕切板14a 、 15a 、、16
a 、 17a 、 18g 、 19aの上部には隣
室との連通口27.29.31.33.35.37が設
けられ、また仕切板14b、 15b、 16b、 1
7b、 18b、 19bの下部には隣室との連通口2
8.30.32.34.36.38が設けられ、汚水が
槽内を下から上に向かって流れるように設計きれている
22, 23, 24, 25, 26 are installed and configured to blow air into the waste water. Partition plate 14a, 1
4b, partition plate 15m, 15b, partition plate 16a, 1
6b, partition plates 17a, 17b, partition plates 18a, 18
b, and the partition plates 19a, 19b are installed with a predetermined spacing, and the partition plates 14a, 15a, 16
A, 17a, 18g, 19a are provided with communication ports 27, 29, 31, 33, 35, 37 at the top thereof, and partition plates 14b, 15b, 16b, 1.
At the bottom of 7b, 18b, and 19b, there is a communication port 2 with the adjacent room.
8, 30, 32, 34, 36, and 38 are provided, and the tank is designed so that the wastewater flows from the bottom to the top.

また仕切板により区画きれた槽の上部には、メツシュの
容器又はパンチングきれた容器4o、42、44.46
.48.50.52が設置きれ、各容器40〜52内に
はそれぞれ、赤玉5.磁鉄鉱石粒9、石灰石粒10、赤
玉5、沸石等の含水硅酸塊粒11、石英粒12、鉄又は
アルミニウムの金属片54が詰め込まれている。56は
処理槽りの排出管であり、4次処理槽Eと連通している
In addition, there are mesh containers or punched containers 4o, 42, 44.
.. 48, 50, 52 are installed, and each container 40-52 has a red ball 5. Magnetite grains 9, limestone grains 10, red beads 5, hydrated silicic acid lump grains 11 such as zeolite, quartz grains 12, and metal pieces 54 of iron or aluminum are packed. 56 is a discharge pipe of the treatment tank, which communicates with the quaternary treatment tank E.

4次処理槽Eは、第6図に示すように仕切板5B、 6
0.62.64により五室に区画されており、仕切板5
8.62の下方には連通用の穴66.68が設けられ、
仕切板60.64の上方には切り欠き70 、72が設
けられている。
The quaternary treatment tank E has partition plates 5B and 6 as shown in FIG.
It is divided into five rooms by 0.62.64, and the partition plate 5
A communication hole 66.68 is provided below 8.62,
Cutouts 70 and 72 are provided above the partition plates 60 and 64.

そして仕切板58.60.62.64により仕切られた
五室にはそれぞれ、赤玉5、沸石等の含水硅酸塊粒11
、海砂74(2層)が充填きれている。
The five chambers partitioned by partition plates 58, 60, 62, and 64 each contain 5 Akadama and 11 hydrated silicic acid lumps such as zeolite.
, the sea sand 74 (two layers) is completely filled.

以上述べた構成において本発明の実施例では、まず原液
調整槽Aにおいて汚水中に空気を噴出きせ懸濁物質を沈
降させる。
In the embodiment of the present invention having the configuration described above, air is first blown into the waste water in the stock solution adjustment tank A to cause the suspended solids to settle.

原液調整槽Aを出た汚水は、1次処理槽Bに導かれ、そ
こで空気を噴出させて汚水を攪拌させながら赤玉5と接
触させる。汚水の奥が赤玉に吸着されると共に2次鉱物
質を1次鉱物質に移行させる(3〜6時間程度)。
The sewage that has come out of the stock solution adjustment tank A is led to the primary treatment tank B, where air is blown out to agitate the sewage and bring it into contact with the red beads 5. The deep part of the sewage is adsorbed by the red beads and the secondary minerals are transferred to the primary minerals (about 3 to 6 hours).

1次処理槽Bを出た汚水は、2次処理層Cに導かれ、汚
水は容器88〜8hに充填きれた赤玉5、礎鉄鉱石粒9
2石灰石粒10.沸石等の含水硅酸塩11、赤玉51石
灰石粒10、石英粒12.赤玉5を通過し、その際に2
次鉱物質を1次鉱物質に移行、汚水中の磁場の安定化、
石灰石粒10による浄化、含水硅酸塩11によるミネラ
ル分の溶出等が行なわれる(4時間程度)。
The sewage that came out of the primary treatment tank B is led to the secondary treatment layer C, and the sewage is collected in containers 88 to 8h filled with Akadama 5 and foundation iron ore grains 9.
2 limestone grains 10. Hydrous silicates such as zeolites 11, Akadama 51, limestone grains 10, quartz grains 12. Pass red ball 5, and at that time 2
Transferring secondary minerals to primary minerals, stabilizing the magnetic field in wastewater,
Purification with limestone grains 10, elution of minerals with hydrated silicate 11, etc. are performed (about 4 hours).

2次処理槽Cにて浄化された水は3次処理槽りニ導カレ
、再び空気の攪拌作用を受けながら赤玉5、磁鉄鉱石粒
9、石灰石粒10、赤玉5、沸石等の含水硅酸塊粒11
、石英粒12、鉄又はアルミニウムの金属片54等と接
触移せられ、2次鉱物質を1次鉱物質に移行、汚水中の
墓場の安定化、石灰石粒10による浄化、含水硅酸塩1
1によるミネラル分の溶出等が行なわれる(6時間程度
)。
The water purified in the secondary treatment tank C is transferred to the tertiary treatment tank, where it is again subjected to the agitation action of air to form hydrated silicic acid such as Akadama 5, magnetite grains 9, limestone grains 10, Akadama 5, and zeolite. lump grain 11
, brought into contact with quartz grains 12, iron or aluminum metal pieces 54, etc., transfers secondary minerals to primary minerals, stabilizes graveyards in sewage, purifies with limestone grains 10, hydrated silicate 1
The elution of minerals in step 1 is carried out (about 6 hours).

3次処理槽りを出た水は4次処理槽Eに導かれ、そして
粘土層を通過して濾過きれた水に含水硅酸塩層でミネラ
ル分を補給し、さらに海砂を通過させることにより塩分
の補給と濾過を行ない浄化を終了する。
The water leaving the tertiary treatment tank is led to the 4th treatment tank E, where it passes through a clay layer, the filtered water is replenished with minerals in a hydrated silicate layer, and is then passed through sea sand. This completes the purification by replenishing salt and filtering.

尚、本実施例では原液処理槽、1次〜4次処理槽を経て
汚水を浄化するように構成したが、これに限定されるも
のではなく汚水の状況等によっては、1次処理槽(赤玉
との接触及び磁鉄鉱石粒との接触)により充分浄化でき
る場合もある。
In this example, the sewage is purified through the undiluted solution treatment tank and the primary to 4th treatment tanks; however, the present invention is not limited to this, and depending on the situation of the sewage, the primary treatment tank (Akadama In some cases, sufficient purification can be achieved by contact with magnetite ore particles).

また汚水の状況が極めて悪い場合には、汚水を各処理槽
において循環するように構成してもよい。CODが高い
場合には3次処理槽りの鉄又はアルミニウム金属片54
の代わりに粘土を用いると良く、化学薬品等を多く含む
汚水の場合は、磁鉄鉱石粒及び石灰石(炭酸カルシウム
)粒を多く用いると良い。
Furthermore, if the condition of the waste water is extremely poor, the waste water may be configured to be circulated in each treatment tank. If COD is high, iron or aluminum metal pieces 54 in the tertiary treatment tank
It is better to use clay instead, and in the case of sewage containing a lot of chemicals, it is better to use a lot of magnetite ore grains and limestone (calcium carbonate) grains.

この実施例にかかる装置を用いて様々な排水について処
理槽をA→B→E(処理方法1)、A→B(第3図の赤
玉の代わりに赤玉60%1石灰30%及び磁鉄鉱石10
%の粒を配合したものを用いた)−E(M理方法2)、
A−B(第3図の赤玉の代わりに赤玉85%及び磁鉄鉱
石15%の粒を配合したものを用いた:)−E(処理方
法3)又はA−B−C→D−E(処理方法4)の順で流
して汚水を処理させる浄化試験を行なった。
Using the apparatus according to this example, treatment tanks for various wastewater were changed from A to B to E (treatment method 1), A to B (instead of Akadama in Figure 3, 60% Akadama, 30% lime, and 10% magnetite ore).
)-E (M method 2),
A-B (A mixture of 85% Akadama and 15% magnetite particles was used instead of the Akadama shown in Figure 3:)-E (Processing method 3) or A-B-C→D-E (Processing method 3) A purification test was conducted in which wastewater was treated by flowing it in the order of method 4).

実施例−1 以下の表−1に示されるクリーニング廃液について、A
4B→Eの処理槽を用いた処理方法1で浄化させたとこ
ろ以下の通りとなった。
Example-1 Regarding the cleaning waste liquid shown in Table-1 below, A
When purified by treatment method 1 using a 4B→E treatment tank, the following results were obtained.

実施例−2 以下の表−2に示される漬物工場廃液についてA−B−
Eの処理槽を用いた処理方法2で浄化許せたところ以下
の表に示す通りとなった。
Example-2 Regarding the pickle factory waste liquid shown in Table-2 below, A-B-
When treatment method 2 using treatment tank E allowed purification, the result was as shown in the table below.

表−2 実施例−3 以下の表−3に示される漬物工場廃液についてA→B→
Eの処理槽を用いた処理方法3で浄化させたところ以下
の表に示す通りとなった。
Table-2 Example-3 Regarding the pickle factory waste liquid shown in Table-3 below, A→B→
When purified by treatment method 3 using treatment tank E, the results were as shown in the table below.

実施例−4 ライスセンターにおける排水を実施例にかかる装置を用
いて処理方法4で浄化させたところ表−4に示す通りと
なった。
Example 4 When wastewater from a rice center was purified by treatment method 4 using the apparatus according to the example, the results were as shown in Table 4.

実施例−5 クリーニング店における排水を実施例にかかる装置を用
いて処理方法4で浄化きせたところ表−5に示す通りと
なった。
Example 5 When wastewater from a cleaning shop was purified by treatment method 4 using the apparatus according to the example, the results were as shown in Table 5.

臀肖− 表−5 実施例−6 クリーニング店における排水を実施例にかかる装置を用
いて処理方法4で浄化させたところ表−6に示す通りと
なった。
Table 5 Example 6 Wastewater from a cleaning shop was purified by treatment method 4 using the apparatus according to the example, resulting in the results shown in Table 6.

実施例−7 化学排水1,2を実施例にかかる装置を用いて処理方法
4で浄化上せたところ表−7に示す通りとなった。
Example 7 Chemical wastewater 1 and 2 were purified by treatment method 4 using the apparatus according to the example, and the results were as shown in Table 7.

実施例−8 化学排水(現像液)における排水を実施例にかかる装置
を用いて処理方法4で浄化させたところ表−8に示す通
りとなった。
Example 8 When chemical waste water (developer) was purified by treatment method 4 using the apparatus according to the example, the results were as shown in Table 8.

効       果 以上述べたように本発明にかかる汚水処理方法は、自然
界に存在する物質を利用してあらゆる種類の汚水を浄化
することができるのでその利用価値は極めて高い。
Effects As described above, the sewage treatment method according to the present invention can purify all kinds of sewage using substances that exist in nature, and therefore has extremely high utility value.

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

第1図から第6図は本発明にかかる実施例を示すもので
、第1図は処理槽の接続関係を示すブロック図、第2図
は原液処理槽Aの縦断面図、第3図は1次処理槽の縦断
面図、第4図は2次処理槽の縦断面図、第5図は3次処
理槽の縦断面図、第6図は4次処理槽の縦断面図である
。 1・・・空気配管    2・・・汚水の供給口3・・
・排出口     4・・・空気配管5・・・赤玉  
    6・・・容器7・・・配管      8・・
・容器9・・・磁鉄鉱石粒   10・・・石灰石粒1
1・・・含水硅酸塩   12・・・石英粒14a〜1
9b・・・仕切板 20〜26空気配管27、29.3
1.3:1.35.37・・・連通口28、30.32
.34.36.38・・・連通口40、42.44.4
6.48.50.52・・・容器54五金属片    
 56・・・排出管58、60.62.64・・・仕切
板 66.68・・・連通用の穴 70.72・・・切り欠
き74・・・海砂
1 to 6 show embodiments of the present invention, in which FIG. 1 is a block diagram showing the connection relationship of processing tanks, FIG. 2 is a longitudinal cross-sectional view of the stock solution processing tank A, and FIG. 3 is a FIG. 4 is a longitudinal sectional view of the primary treatment tank, FIG. 4 is a longitudinal sectional view of the secondary treatment tank, FIG. 5 is a vertical sectional view of the tertiary treatment tank, and FIG. 6 is a vertical sectional view of the tertiary treatment tank. 1...Air piping 2...Sewage supply port 3...
・Exhaust port 4...Air pipe 5...Red ball
6... Container 7... Piping 8...
・Container 9... Magnetite grains 10... Limestone grains 1
1... Hydrous silicate 12... Quartz grains 14a-1
9b...Partition plate 20-26 Air piping 27, 29.3
1.3:1.35.37...Communication port 28, 30.32
.. 34.36.38...Communication port 40, 42.44.4
6.48.50.52... Container 54 5 metal pieces
56...Discharge pipe 58, 60.62.64...Partition plate 66.68...Communication hole 70.72...Notch 74...Sea sand

Claims (5)

【特許請求の範囲】[Claims] (1)汚水をアルミノ硅酸塩を含有した粘土を造粒して
なる赤玉と接触させる工程と、汚水を磁鉄鉱石粒と接触
させる工程とからなる汚水の浄化方法。
(1) A method for purifying sewage comprising the steps of bringing the sewage into contact with red beads made by granulating clay containing aluminosilicate, and bringing the sewage into contact with magnetite ore grains.
(2)各接触工程において、空気を汚水中に噴出させな
がら空気攪拌を行なう請求項1記載の汚水の浄化方法。
(2) The method for purifying wastewater according to claim 1, wherein air is stirred while blowing air into the wastewater in each contact step.
(3)汚水をアルミノ硅酸塩を含有した粘土を造粒して
なる赤玉と接触させる工程と、汚水を磁鉄鉱石粒と接触
させる工程と、汚水を鉄又はアルミニウム金属と接触さ
せる工程と、汚水をゼオライト等の含水硅酸塩と接触さ
せる工程と、汚水を石灰石等の炭酸カルシウムと接触さ
せる工程とからなる汚水の浄化方法。
(3) A step of bringing the sewage into contact with red beads made by granulating clay containing aluminosilicate, a step of bringing the sewage into contact with magnetite ore grains, a step of bringing the sewage into contact with iron or aluminum metal, and a step of bringing the sewage into contact with iron or aluminum metal; A method for purifying sewage comprising the steps of bringing the sewage into contact with a hydrous silicate such as zeolite, and bringing the sewage into contact with calcium carbonate such as limestone.
(4)各接触工程において、空気を汚水中に噴出させな
がら空気攪拌を行なう請求項3記載の汚水の浄化方法。
(4) The method for purifying wastewater according to claim 3, wherein air is stirred while blowing air into the wastewater in each contact step.
(5)汚水を海砂と接触させる工程を含む請求項3記載
の汚水の浄化方法。
The method for purifying wastewater according to claim 3, comprising the step of (5) bringing the wastewater into contact with sea sand.
JP32643390A 1990-11-28 1990-11-28 Method for purifying sewage Pending JPH04193387A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP32643390A JPH04193387A (en) 1990-11-28 1990-11-28 Method for purifying sewage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP32643390A JPH04193387A (en) 1990-11-28 1990-11-28 Method for purifying sewage

Publications (1)

Publication Number Publication Date
JPH04193387A true JPH04193387A (en) 1992-07-13

Family

ID=18187752

Family Applications (1)

Application Number Title Priority Date Filing Date
JP32643390A Pending JPH04193387A (en) 1990-11-28 1990-11-28 Method for purifying sewage

Country Status (1)

Country Link
JP (1) JPH04193387A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3005069U (en) * 1994-06-08 1994-12-06 高砂熱学工業株式会社 Anticorrosion device for piping system connected to heat storage tank
JPH0739994U (en) * 1993-12-29 1995-07-18 重春 中尾 Septic tank
JP2008264622A (en) * 2007-04-17 2008-11-06 Tochigi Prefecture Wastewater purifying apparatus
JP2010000416A (en) * 2008-06-18 2010-01-07 Ohbayashi Corp Treatment method, treatment material and treatment apparatus for heavy metal contaminated water, and treatment method, treatment material and treatment apparatus for arsenic contaminated water
CN102730915A (en) * 2012-07-13 2012-10-17 中科同创(厦门)环境科技有限公司 Dispersive sewage multilayer soil ecological treatment device and method
JP2013099751A (en) * 2013-03-05 2013-05-23 Ohbayashi Corp Method and apparatus for treating arsenic contaminated water

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0739994U (en) * 1993-12-29 1995-07-18 重春 中尾 Septic tank
JP3005069U (en) * 1994-06-08 1994-12-06 高砂熱学工業株式会社 Anticorrosion device for piping system connected to heat storage tank
JP2008264622A (en) * 2007-04-17 2008-11-06 Tochigi Prefecture Wastewater purifying apparatus
JP2010000416A (en) * 2008-06-18 2010-01-07 Ohbayashi Corp Treatment method, treatment material and treatment apparatus for heavy metal contaminated water, and treatment method, treatment material and treatment apparatus for arsenic contaminated water
CN102730915A (en) * 2012-07-13 2012-10-17 中科同创(厦门)环境科技有限公司 Dispersive sewage multilayer soil ecological treatment device and method
JP2013099751A (en) * 2013-03-05 2013-05-23 Ohbayashi Corp Method and apparatus for treating arsenic contaminated water

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