JPS58166914A - Treatment of waste water - Google Patents

Treatment of waste water

Info

Publication number
JPS58166914A
JPS58166914A JP57049151A JP4915182A JPS58166914A JP S58166914 A JPS58166914 A JP S58166914A JP 57049151 A JP57049151 A JP 57049151A JP 4915182 A JP4915182 A JP 4915182A JP S58166914 A JPS58166914 A JP S58166914A
Authority
JP
Japan
Prior art keywords
waste water
settling
filter
basin
tank
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.)
Granted
Application number
JP57049151A
Other languages
Japanese (ja)
Other versions
JPS6034886B2 (en
Inventor
Toshiyuki Yokoyama
横山 寿幸
Shinichi Shimada
信一 島田
Suguru Kamakura
鎌倉 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.)
Sumitomo Heavy Industries Ltd
Tsukishima Kikai Co Ltd
Original Assignee
Sumitomo Heavy Industries Ltd
Tsukishima Kikai 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 Sumitomo Heavy Industries Ltd, Tsukishima Kikai Co Ltd filed Critical Sumitomo Heavy Industries Ltd
Priority to JP57049151A priority Critical patent/JPS6034886B2/en
Publication of JPS58166914A publication Critical patent/JPS58166914A/en
Publication of JPS6034886B2 publication Critical patent/JPS6034886B2/en
Expired legal-status Critical Current

Links

Abstract

PURPOSE:To decrease the volume of a flocculating and settling basin and to reduce the size of waste water treatment facilities by incorporating a filter device provided with a moving bed type filter machine in waste water treatment stages. CONSTITUTION:Waste water is supplied through a dust removing device 1 using grit into a preliminary aeration tank 2, where the materials that settle are made easier to settle and the materials that suspend are made easier to suspend. The aerated water is fed into a settling basin 3. The overflow liquid from the basin 3 is fed to an aeration tank 4, where the sludge contg. microorganisms and air are mixed therewith under stirring and the water in the state vulnerable to settling is subjected to settling in a final settling basin 5a. The size of the basin 5a is made smaller by about 50% as compared to the prior art. A filter device 9 requiring relatively small installation volume is placed, and the sludge is filtered and recovered with said device, whereafter the waste water is sterilized with a sterilizer 6 to clean water. A moving bed type filter machine which uses combustible filter media such as pulverized coal and in which the filter media are moved by the lower part of the filter tank is used for the device 9.

Description

【発明の詳細な説明】 本発明は産業排水、下水、し尿等を浄化処理する排水処
理方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a wastewater treatment method for purifying industrial wastewater, sewage, human waste, and the like.

従来排水処理は第1図に示す如く、まず沈砂、除塵装置
1で砂、ごみ等を除去したのち、予備曝気槽2に送られ
る。こ\で空気を吹き込んで攪拌処理され、沈むものは
沈み易く、浮遊するものは浮き易くして、次の最初沈澱
池3に送られ、水面に浮いたゴミは機械で掻集めて取シ
除き、沈んだ汚泥は池の底で掻き集められポンプで抜き
とる。
In conventional wastewater treatment, as shown in FIG. 1, first, sand, dust, etc. are removed by a sand settling and dust removal device 1, and then the wastewater is sent to a preliminary aeration tank 2. Air is blown in and agitated to make things that sink easier to sink and things that float easier to float, and then sent to the first sedimentation tank 3, where debris floating on the water surface is scraped up and removed by a machine. The settled sludge is scraped up at the bottom of the pond and pumped out.

沈澱池3を経た排水は曝気槽4に送られて微生物を含ん
だ泥水と空気を混入して攪拌され、微生物は下水中の有
機物、質を餌にし水中の溶存酸素をとって増殖し、沈澱
し易くされ、最終沈澱池5で沈澱する。最終沈澱池5を
出た排水は滅菌装置6で大腸菌等の細菌を滅菌したのち
浄水として再利用されるか又は川へ放流される。
The wastewater that has passed through the sedimentation tank 3 is sent to the aeration tank 4, where it is mixed with muddy water containing microorganisms and air and stirred.The microorganisms feed on the organic matter in the sewage, take dissolved oxygen from the water, multiply, and settle. and is precipitated in the final settling tank 5. The wastewater discharged from the final settling tank 5 is sterilized from bacteria such as E. coli in a sterilizer 6, and is then reused as purified water or discharged into the river.

一方最初沈澱池で沈澱した汚泥及び最終沈澱池で沈澱し
た活性汚泥は汚泥処理装@ 7 、たとえば濃縮槽、消
化槽、凝集槽、乾燥機等を経て埋立又は焼却処理される
。なお活性汚泥の一部は配管8を経て曝気槽4に返送さ
れ、余剰のもののみ前記汚泥処理装置7に送られる。
On the other hand, the sludge settled in the first settling tank and the activated sludge settled in the final settling tank are sent to a sludge treatment device, such as a thickening tank, a digestion tank, a flocculating tank, a dryer, etc., and are then landfilled or incinerated. A part of the activated sludge is returned to the aeration tank 4 via the pipe 8, and only the surplus is sent to the sludge treatment device 7.

さて斜上の如き処理プロセスに於て、BoD、 CoD
物質を、不溶性の形態即ち固体と衿排水中より分離する
沈澱工程で、生物化学的処理を適用し、バクテリヤの働
きで生成したフロック状固体を排水よシ分離する為、凝
集沈澱池が一般に用いられている。しかしこの沈澱池は
その容積が排水処理工程の司成りの部分を占めるので、
処理設備として膨大な敷地?要するという、不都合があ
った。
Now, in the processing process as shown above, BoD, CoD
In the sedimentation process, which separates substances from insoluble forms, i.e., solids, from the wastewater, a coagulation sedimentation tank is generally used to apply biochemical treatment and separate floc-like solids generated by the action of bacteria from the wastewater. It is being However, since the volume of this sedimentation tank is the main part of the wastewater treatment process,
Huge amount of land for processing equipment? There was an inconvenience.

本発明はこの排水処理工程中に移動床式p過層を備えた
濾過装置を組込むことにより、前記凝集沈澱池の容極を
50%以下となし、全体的に排水処理施設の縮少化を図
ろうとするものでちる。
The present invention incorporates a filtration device equipped with a moving bed type p-filter into this wastewater treatment process, thereby reducing the capacity of the coagulation sedimentation tank to 50% or less, thereby reducing the overall size of wastewater treatment facilities. It's what I'm trying to figure out.

第2図は本発明に係る排水処理方法を示し、沈砂除塵装
置1を経て予備曝気槽2に入りこ\で沈澱するものは沈
澱し易く、浮遊するものは浮き易くして最初沈澱池3に
送シ込むまでは第1図の従来例と全く同一である。
Fig. 2 shows the wastewater treatment method according to the present invention, in which the wastewater that enters the preliminary aeration tank 2 via the sand settling and dust removal device 1 is easily settled, and the floating waste is made easy to float and is first transferred to the settling tank 3. The process up to the feeding is completely the same as the conventional example shown in FIG.

さて最初沈澱池3の溢流液は曝気槽4に送られ、こ\で
微生物を含んだ泥水と空気を混入して攪拌され、沈澱し
易くなった状態で最終沈澱池5aで沈澱処理される。
First, the overflow from the sedimentation tank 3 is sent to the aeration tank 4, where it is mixed with muddy water containing microorganisms and air, stirred, and in a state where it becomes easier to settle, it is subjected to sedimentation treatment in the final sedimentation tank 5a. .

この最終沈澱池5aは第1の場合と比較し、その大きさ
は約50%と縮少されている。沈澱物の縮少化に伴いこ
の沈澱池における排水中の汚泥回収率が低下するのは当
然であるが、本発明に於てはこの次に比較的設置容積會
とらない濾過装置9を置き、これによって汚泥を濾過回
収し、このあと排水を滅菌装置6を経て浄水としている
The size of this final settling tank 5a is reduced by about 50% compared to the first case. It is natural that the sludge recovery rate in the wastewater in this sedimentation tank decreases as the sediment decreases, but in the present invention, next to this is a filtration device 9 that takes up a relatively small installation volume. As a result, the sludge is filtered and recovered, and then the waste water is passed through the sterilizer 6 to be purified water.

濾過装置9は微粉炭等の可燃性炉材を使用し、濾過槽下
部に設けられたロータリーフィーダ10等によって濾過
材を移動させ、排水の通過する部分は常に濾過可能にし
ておくいわゆる連続運転可能な移動床弐濾過機が使用さ
れる。
The filtration device 9 uses combustible furnace material such as pulverized coal, moves the filtration material by a rotary feeder 10, etc. provided at the bottom of the filtration tank, and is capable of so-called continuous operation in which the portion through which wastewater passes can always be filtered. A moving bed filtration machine is used.

本処理方法の適用範囲は、曝気槽のオーバーフロー水の
水質がBoD、 −CoDで2,000〜3,000p
pm、88(固形物質)で2,000〜3,000 p
pm程度の場合、実験によれば凝集沈澱池の容積を通常
必要とされる容積の1/4に圧縮した場合、凝集沈澱池
出口側の溢流水の水質はBoD、 CoD 1,000
ppm以下、SS  l、000 ppm以下となり、
この程度の水質であれば移動床式瀘過装置で連続的に処
理することは可能である。そして、必要に応じこの移動
床式沖過装置を縦設すれば、さらに十分なp過動率を得
ることができる。
The scope of application of this treatment method is that the quality of the overflow water from the aeration tank is BoD, -CoD, 2,000 to 3,000p.
pm, 2,000-3,000 p at 88 (solid material)
pm, experiments have shown that when the volume of the coagulation and sedimentation tank is compressed to 1/4 of the normally required volume, the quality of the overflow water at the outlet of the coagulation and sedimentation tank is BoD, CoD 1,000.
ppm or less, SS l, 000 ppm or less,
If the water quality is at this level, it is possible to treat it continuously using a moving bed type filtration device. Further, by vertically installing this movable bed-type off-shore passing device as necessary, a more sufficient p-overmovement rate can be obtained.

濾過装置の容積は凝集沈澱池に比し、大巾に小さくなる
。凝集沈澱池の容積を半減することができれば、新たに
追加される移動床式濾過装置を差引いても、全体からみ
ると、設備所要面積が縮少でき、これらの排水処理設備
に対する投資額を軽減できる。と共にランニングコスト
をも大巾に低減することができる。
The volume of the filtration device is much smaller than that of the coagulation sedimentation tank. If the volume of the coagulation and sedimentation basin can be halved, even after subtracting the newly added moving bed filtration equipment, the area required for the equipment can be reduced overall, reducing the investment amount for these wastewater treatment equipment. can. At the same time, running costs can also be significantly reduced.

移動床式−過装置にはその胛材として活性炭、廟プラス
チック、石灰層等の可燃性材が使用される。従って廃棄
物の有効□利用に役立つと共に、この胛材に吸着、捕集
される排水中の浮遊固形物はP材とともに乾燥され、最
終的に燃料として有効利用される゛。
The movable bed type filtration equipment uses combustible materials such as activated carbon, mausoleum plastic, limestone layer, etc. Therefore, it is useful for the effective use of waste materials, and the suspended solids in the wastewater that are adsorbed and collected by this material are dried together with the P material and finally used effectively as fuel.

炉材の粒子径は0.1−〜io++msのものを炉材の
種類、排水の水質、放流基準等によシ、最も適当なもの
を選択使用すべきであるが、移動床式涙過装置を用いる
ため、p過層を原水側と処理水側に異った粒子径の炉材
又は異った種類のp材會組合わせることによって優れた
濾過性能が得られるよう調整できる。又、移動床式渥過
装置を用いるので、炉材の洗浄工程を要せず、固定床式
p過装置に較べ処理能力は大きく、連続して、安定した
濾過性能が得られる。
The particle size of the furnace material should be 0.1-io++ ms depending on the type of furnace material, waste water quality, discharge standards, etc., and the most appropriate one should be selected and used. Therefore, it is possible to adjust the p-filtration layer to obtain excellent filtration performance by combining furnace materials with different particle sizes or different types of p-materials on the raw water side and the treated water side. Furthermore, since a moving bed type filtering device is used, there is no need for a cleaning process for the furnace material, the processing capacity is greater than that of a fixed bed type filtering device, and continuous and stable filtration performance can be obtained.

尚、凝集沈澱池の容積を縮少し、これに代え移動床式濾
過装置を用いだので、最終沈澱池に沈澱する活性汚泥の
量は減シ、配管8t−経て曝気槽に返送される分を除い
た余剰汚泥の量は極めて少量となるから、汚泥処理装置
も小型化できる
Furthermore, by reducing the volume of the coagulation sedimentation tank and replacing it with a moving bed type filtration device, the amount of activated sludge that settles in the final sedimentation tank is reduced, and the amount returned to the aeration tank via 8 tons of piping is reduced. Since the amount of excess sludge removed is extremely small, the sludge treatment equipment can also be downsized.

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

第1図は従来公知の排水処理装置を示す。 第2図は本発明に係る排水処理方法を実施するだめの装
置の一例を示す。 図において、 1 沈砂除塵装置   2 予備曝気槽3 最初沈澱池
    4 曝気槽 5 最終沈澱池   5a  (本発明の)最終沈澱池 6 滅菌装置     I 汚泥処理装置8 配管  
     9 濾過装置 10 ロータリーフィーダ 以    上
FIG. 1 shows a conventionally known wastewater treatment device. FIG. 2 shows an example of a device for carrying out the wastewater treatment method according to the present invention. In the figure, 1 sand and dust removal device 2 preliminary aeration tank 3 first settling tank 4 aeration tank 5 final settling tank 5a (of the present invention) final settling tank 6 sterilization device I sludge treatment device 8 piping
9 Filtration device 10 Rotary feeder or above

Claims (1)

【特許請求の範囲】[Claims] 物理処理、生物化学処理をしたのちの処理水中に存在す
る汚濁物質を凝集沈澱池を用いて固液分離する方法にお
いて、小型の凝集沈澱池を設け、その後段に可燃性濾過
機で形成される層状濾過床會肩する移動床式濾過装置を
用いて濾過するようにしたことを特徴とする排水処理方
法。
In a method of solid-liquid separation of pollutants present in treated water after physical treatment and biochemical treatment using a coagulation sedimentation tank, a small coagulation sedimentation tank is installed, followed by a combustible filter. A wastewater treatment method characterized in that filtration is carried out using a moving bed type filtration device having a layered filtration bed.
JP57049151A 1982-03-29 1982-03-29 Wastewater treatment method Expired JPS6034886B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57049151A JPS6034886B2 (en) 1982-03-29 1982-03-29 Wastewater treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57049151A JPS6034886B2 (en) 1982-03-29 1982-03-29 Wastewater treatment method

Publications (2)

Publication Number Publication Date
JPS58166914A true JPS58166914A (en) 1983-10-03
JPS6034886B2 JPS6034886B2 (en) 1985-08-12

Family

ID=12823092

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57049151A Expired JPS6034886B2 (en) 1982-03-29 1982-03-29 Wastewater treatment method

Country Status (1)

Country Link
JP (1) JPS6034886B2 (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102407048A (en) * 2011-09-29 2012-04-11 山西潞安环保能源开发股份有限公司 Underground coal slime water processing system
CN102923908A (en) * 2012-10-30 2013-02-13 刘贤斌 Sewage biochemical treatment integrated device and system and process method
CN104117242A (en) * 2014-07-11 2014-10-29 福建省永安林业(集团)股份有限公司 A treatment device for wood chip washing waste water and exhaust
CN104174219A (en) * 2014-08-29 2014-12-03 玖龙纸业(太仓)有限公司 Treatment device of ink on waste paper
CN104492158A (en) * 2014-11-11 2015-04-08 无锡市张泾机械设备厂 Waste water sedimentation basin
CN105169806A (en) * 2015-10-27 2015-12-23 丁西军 Stone processing sewage treatment system
CN106830430A (en) * 2017-03-07 2017-06-13 李如意 The efficient fast treating process and method of a kind of low temperature and low turbidity water
CN111675400A (en) * 2020-06-17 2020-09-18 苏波 Sewage purification treatment device

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08155149A (en) * 1994-12-02 1996-06-18 Nakashiyou Giken:Kk Doll

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102407048A (en) * 2011-09-29 2012-04-11 山西潞安环保能源开发股份有限公司 Underground coal slime water processing system
CN102923908A (en) * 2012-10-30 2013-02-13 刘贤斌 Sewage biochemical treatment integrated device and system and process method
CN104117242A (en) * 2014-07-11 2014-10-29 福建省永安林业(集团)股份有限公司 A treatment device for wood chip washing waste water and exhaust
CN104174219A (en) * 2014-08-29 2014-12-03 玖龙纸业(太仓)有限公司 Treatment device of ink on waste paper
CN104492158A (en) * 2014-11-11 2015-04-08 无锡市张泾机械设备厂 Waste water sedimentation basin
CN105169806A (en) * 2015-10-27 2015-12-23 丁西军 Stone processing sewage treatment system
CN106830430A (en) * 2017-03-07 2017-06-13 李如意 The efficient fast treating process and method of a kind of low temperature and low turbidity water
CN106830430B (en) * 2017-03-07 2021-02-09 李如意 Efficient and rapid treatment process and method for low-temperature and low-turbidity water
CN111675400A (en) * 2020-06-17 2020-09-18 苏波 Sewage purification treatment device

Also Published As

Publication number Publication date
JPS6034886B2 (en) 1985-08-12

Similar Documents

Publication Publication Date Title
US4200524A (en) Bio-surface separation process
KR100851456B1 (en) Method and apparatus for treatment of water
JPS6230597A (en) Method of separating clarified liquid from biomass on biological treatment of waste water
CA2625798A1 (en) Water treating method and arrangement integrating a fixed-bacteria biological treatment and flocculation-decantation
US20020166819A1 (en) System and method for separating components of liquid manure
JPS58166914A (en) Treatment of waste water
JP4144952B2 (en) Purification methods for rivers and lakes
JP3797296B2 (en) Purification method of bottom sludge
JP5225307B2 (en) Phosphorus recovery equipment
US3835038A (en) Activated sewage plant and process
KR100920454B1 (en) Sewage disposal plant sewage disposal method
KR102009674B1 (en) Eco-friendly living sewage treatment system
JPS58166915A (en) Treatment of waste water
KR100385417B1 (en) Apparatus for Advanced Treatment of BOD in Sewage and Dirty Water
SU1000422A1 (en) Method and apparatus for purifying effluents
JP4549000B2 (en) Water purification equipment for suspended solids
KR101745347B1 (en) Wastewater treatment equipment and treatment method thereof
JP3270155B2 (en) Sewage treatment method and treatment device
JP4302786B2 (en) High SS waste liquid and sludge purification method
JPH06170398A (en) Treatment of sludge containing blast furnace water slag in activated sludge treatment
JPS57117400A (en) Dehydration of excessive sludge
KR100614742B1 (en) A method of water purification using olivine
SU688444A1 (en) Method of purifying surface water
JP3731796B2 (en) Method and apparatus for treating water containing organic matter
RU1835389C (en) Technique of water purification