JPS59209699A - Filthy water disposal - Google Patents

Filthy water disposal

Info

Publication number
JPS59209699A
JPS59209699A JP58082300A JP8230083A JPS59209699A JP S59209699 A JPS59209699 A JP S59209699A JP 58082300 A JP58082300 A JP 58082300A JP 8230083 A JP8230083 A JP 8230083A JP S59209699 A JPS59209699 A JP S59209699A
Authority
JP
Japan
Prior art keywords
sludge
oxygen
carbon powder
tank
filthy water
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
JP58082300A
Other languages
Japanese (ja)
Inventor
Yoshihiro Watanabe
渡辺 佳弘
Hideyoshi Matsubara
秀吉 松原
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.)
Ishigaki Mechanical Industry Co Ltd
Original Assignee
Ishigaki Mechanical Industry 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 Ishigaki Mechanical Industry Co Ltd filed Critical Ishigaki Mechanical Industry Co Ltd
Priority to JP58082300A priority Critical patent/JPS59209699A/en
Publication of JPS59209699A publication Critical patent/JPS59209699A/en
Pending legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Activated Sludge Processes (AREA)

Abstract

PURPOSE:To consistently perform filthy water disposal and sludge disposal for contriving the improvement in the efficiency of disposal, by subjecting filthy water being mixed with powdery carbon particles to biochemical treatment using air, adding a combustible coagulant to excess sludge, and burning cake after being dehydrated. CONSTITUTION:Filthy water is continuously or intermittently mixed with powdery carbon particles in a conduit 1, introduced into an aerator tank 3 and aerated therein with air or oxygen-rich air. The interior of the tank 3 is made aerobic to decompose organic substance existent in filthy water with microbes implanted on the introduced powdery carbon particles. Hence, the filthy water is purified. The treated water together with sludge is then introduced into a precipitation tank 6 to separately precipitate solid matter. Excess sludge is introduced into a sludge reservoir tank 10, a combustible macromolecular coagulant is further added in a conduit 12, and then the sludge is supplied to a dehydrator 13. Dehydrated cake is carried to a burning oven 15 and burnt therein. Oxygen-contg. waste gas from the aerator tank 3 is introduced into the burning oven 15 to use the oxygen incorporated in said waste gas oxygen for combustion.

Description

【発明の詳細な説明】 本発明は、汚水の生物化孝的処l、!I!方法と、該余
剰汚泥の処理に関するものでめる。
DETAILED DESCRIPTION OF THE INVENTION The present invention provides a biological treatment for wastewater. I! This article describes methods and treatment of excess sludge.

汚水の生物化学的処理には、曝気和尚に浮遊しゾこ好気
性微生物によシ、肩磯物を分M浄化するン古、曝気槽内
の微生物量を一定限度以上高くでさず、そのため、処理
能力に限界が8つだ。
For biochemical treatment of sewage, aerobic microorganisms floating in the aeration tank are used to purify the debris, and the amount of microorganisms in the aeration tank is not raised above a certain limit. , there are eight limits to processing power.

近時、この様な活性汚泥の欠点を改良し、即ノjの安定
と向上を目的として、曝気槽内σ〕做/+吻す〕着床面
積を多くしたり、発生汚泥の沈降1生σノly、善等を
目的として粒状物を曝気槽に混入し、生物化学的処理を
行う流動床式活性/ri泥法が提供され始めている。こ
の方法には、流動媒体を曝気4゛曽内に常時留め、流動
媒体よシ剥離した余剰汚泥を、曝気槽外へ排出する方法
と、従来の活性汚泥と同4子に、流動媒体と汚泥を混合
状態のままI曝気惜よυ排出して、沈殿槽で沈降分離し
た汚泥の一部を幡気慴に返送し、残余のものを余剰汚泥
とする方法がある。
Recently, with the aim of improving the shortcomings of activated sludge and stabilizing and improving the immediate production, efforts have been made to increase the settling area in the aeration tank and to reduce the sedimentation rate of generated sludge. A fluidized bed activated/RI mud method is beginning to be provided in which granular materials are mixed into an aeration tank and biochemically treated for the purpose of improving sigma. This method involves keeping the fluidized medium in the aeration chamber at all times and discharging excess sludge separated from the fluidized medium to the outside of the aeration tank. There is a method in which the sludge is discharged in a mixed state, separated by sedimentation in a settling tank, and a portion of the sludge is returned to the tank, and the remaining sludge is used as surplus sludge.

流動媒体を曝気横内に留める前者σ)方法でC−1、流
動媒体として、従来、活性炭1石炭コークス。
In the former σ) method in which the fluidizing medium is kept within the aeration side, C-1, the fluidizing medium is conventionally activated carbon 1 coal coke.

砂等が用いられるが、いずれも、曝気槽より流出しない
ように、流動媒体の最低粒径を限定したり−−曝気槽構
造及び該溢流部を工夫する必要かめに対して維持管理が
煩しい欠点がおった。
Sand, etc. are used, but in either case, the minimum particle size of the fluidizing medium must be limited to prevent it from flowing out of the aeration tank -- the structure of the aeration tank and the overflow area must be devised, and the maintenance and management of the tank is complicated. There was a new drawback.

一方、流MilJ媒体を汚泥と混合状態のまま曝気槽よ
す流出させる後者の方法では、従来、流動媒体として粉
末活性炭及び粘土粉等が知られている。
On the other hand, in the latter method, in which the flowing MilJ medium is flowed out of the aeration tank in a mixed state with sludge, powdered activated carbon, clay powder, etc. are conventionally known as the fluidizing medium.

この場合には、余剰汚泥と混合状態で排出される流動媒
体に見合った量を、曝気槽への汚水の流入に応じて追加
補給する必要がらる。しかしながら、流動媒体として粉
末γ占性炭な使用した場合には、活性炭自体の物理化学
的吸〃i作用(でよる浴甫′成分の浄化効果も多少ある
が、活性炭自体が?、あIUl+なだめに、汚泥より分
層[シ、丹生俊、再4り用しなければフスト高となり、
なた、再生するIIこしても壊6、l装置が併設される
必要がらり、再生費用も安価でない。また、粘土扮専を
流動媒体とした場合には、活性炭種流動媒体としてのコ
スト11かからないが、粘土粉癌加ンこよる汚泥扇の増
加はまぬがれ得す、投棄費用が高くなる欠点があり、ま
た、該汚泥を焼却するにしても、粘土粉による無機質の
増加で、汚泥の発熱量が低下し、助燃剤が多く必要とな
り、さらに、焼却後の灰分の増加をまね体として使用す
るには複雑な装置が必要でめり、  1維持管理がむず
かしく、また、汚泥と混合状態のままで処分するにして
も、汚泥J(tが増加し、流動媒体の費用も含めて処理
費用がかさむ欠点がりって、bIL励床式活注lυ泥法
は余ジ広く採用されなかった。
In this case, it is necessary to additionally replenish an amount commensurate with the amount of fluidized medium discharged in a mixed state with surplus sludge in accordance with the flow of wastewater into the aeration tank. However, when powdered γ-occupied charcoal is used as a fluid medium, the activated carbon itself has a physicochemical adsorption effect (due to its purifying effect on the bath gas component), but the activated carbon itself has a In addition, if the sludge is separated from the sludge and is not reused, it will become more expensive.
In addition, it is necessary to install a device to reproduce the equipment, and the recycling cost is not cheap. In addition, when clay is used as a fluid medium, it does not cost as much as an activated carbon type fluid medium, but it has the disadvantages that the increase in sludge caused by the addition of clay powder can be avoided and the disposal cost increases. In addition, even if the sludge is incinerated, the calorific value of the sludge decreases due to the increase in inorganic content due to clay powder, and a large amount of combustion improver is required.Furthermore, the increased ash content after incineration makes it difficult to use it as a mimic. It requires complicated equipment, is difficult to maintain, and even if it is disposed of as it is mixed with sludge, the sludge J(t) increases, which increases the processing cost including the cost of the fluidizing medium. For this reason, the bIL excited bed live pouring mud method was not widely adopted.

一方、汚水の生物化学的処理よV発生する汚泥の処分法
として、農地への還元、埋め立て役菓。
On the other hand, as a method of disposing of the sludge generated by biochemical treatment of sewage, it can be returned to farmland or landfilled.

保が次第に難しくなシつつあり、かつ、有機質の多い生
物化学的処理汚泥は、造成池としては軟弱であり、しか
も悪臭を放ち、必ずしも良好な方法とはいえず、環境面
からも未処理汚泥の投束は間:億があった。
Biochemically treated sludge, which is becoming increasingly difficult to maintain and contains a large amount of organic matter, is too soft for use in ponds and emits a foul odor, so it is not necessarily a good method, and untreated sludge is not suitable for environmental reasons. The investment amount was 100 million.

この様な問題に対する一つの対応−策として、脱水ケー
キを焼却、灰化して投挺する方法が採用きれる小が多く
なった。しかしながら、脱水ケーキ・の焼却においては
、条材の助燃剤、主に重油が必要でめり、燃′4+萱高
1虜の折柄、費用面で可成シの負担を強いしオしていた
As one measure to deal with these problems, many small schools have adopted the method of incinerating the dehydrated cake, turning it into ashes, and then dumping it. However, when incinerating dehydrated cakes, a combustion aid for the strips, mainly heavy oil, is required. Ta.

一部に、生物化学的処理汚泥はρ過性が恐く、圧縮率も
高いため、I濾過ケーキ中の水分含有率が高く、燃料費
の増大にもなっていた。そこで、効率良い脱水処理を行
うために、鑓果削やr濾過助バ・jを用いて脱水処理す
る必要が必ジ、これ址で幾多の方法が提案、採用δれで
さた。これしり〕うち、現在、生に採用されている楓化
粥二秩と消石灰を添加する方法V1、良好な脱水性と苫
水率のはい脱、多J11の助燃剤が心安でめり、かつ、
焼却員の灰分が多くなシ、式ら1cは、六1(1hクロ
ムが発生する問題が8つだ。一方、M機糸の、湧分子嵯
集i41またけを用いて脱水処理する方法では、7A却
佼の灰分の増加はないが、脱水ケーキの含水率が高く、
そのケーキ中の水分の蒸発に熱を消〆綺され、ケーキの
燃焼時の発熱量はそれ自身が目燃する程高くならず、や
はり助燃剤が必要でのった。
In part, biochemically treated sludge has poor permeability and high compressibility, resulting in a high water content in the I-filtration cake, which also increases fuel costs. Therefore, in order to carry out efficient dehydration treatment, it is necessary to perform dehydration treatment using shavings or a filter aid, and a number of methods have been proposed and adopted. Among them, method V1 of adding maple porridge Nichichi and slaked lime, which is currently used for raw, has good dehydration properties and low water rate, and the combustion improver of poly J11 is safe and easy to use. ,
Shiki et al. 1c has a large amount of ash from the incineration workers, and there are 8 problems in which 61 (1h chromium) is generated.On the other hand, M machine's method of dehydration treatment using Yuki Mosaishu i41 straddle , there is no increase in ash content in 7A Luo, but the moisture content of the dehydrated cake is high;
The heat was dissipated by the evaporation of water in the cake, and the calorific value of the cake itself was not high enough to cause combustion, so a combustion improver was still required.

近来、これらの汚泥処理の改良法として可燃性であり、
かつ、剛性の高い倣粉炭9石炭コークス・石油コークス
等の濾過助剤と、可燃性の有様高分子凝集剤を用いて脱
水し、その脱水ケーキもテ埼ノ、11する方法が提案さ
れている。この方法は、濾過助11すの剛性が、;7i
い/こめ、高圧3’j r高脱水が円曲と・クジ、C′
□進71jJ局i住の馬Z尼でも良好e?戸〕尚性化を
イく+ることがでさ5.配水ケーキの言水率が低く、か
つ、0−′:lI→助J−tl」rは果剤がいずれもロ
エ慾性の/こめVC1自悠件の発熱蛍の商い脱水ケーキ
ン、74ることかでさ、その脱水ケーキを焼却する場合
に、重油等の助法でるる。
Recently, as an improved method for treating these sludges, flammable and
In addition, a method has been proposed in which dehydration is performed using a filter aid such as highly rigid pulverized coal9 coal coke or petroleum coke and a flammable polymer coagulant, and the resulting dehydrated cake is also removed. There is. In this method, the rigidity of the filter aid 11 is;
I/Kome, high pressure 3'j r high dehydration is circular and Kuji, C'
□Shin 71j J station i resident horse Zuni is also good e? 5. It is possible to become sexually active. The water rate of the water distribution cake is low, and 0-':lI→sukeJ-tl'r means that the fruit is all about Roe's desire/Kome VC1's free fever firefly trade dehydration cake, 74 However, when incinerating the dehydrated cake, you can use heavy oil or other auxiliary methods.

しかしながら、この方法に、汚泥の脱水と焼却処理のみ
考慮した方式でりp2汚泥の発生源である汚水の生物化
学的処理方法にかかわらず、を濾過工8直前に濾過助剤
として炭素粉粒を特別に協力1する必要があった。
However, this method only takes into consideration the dewatering and incineration of sludge, and regardless of the biochemical treatment method for sewage that is the source of P2 sludge, carbon powder is added as a filter aid immediately before the filter step 8. Special cooperation was required.

本発明の意図する東1の目的は、汚水の生物化学的処理
工程と該汚泥の濾過工程及び燃焼処理工程を通じての一
貫したプロセスとしての効率の向上と、処理費用の低減
を可能ならしめる省エネルギー汚水処理γステムを提供
する事に必る。
The first object of the present invention is to improve the efficiency of a consistent process through the biochemical treatment process of sewage, the filtration process of the sludge, and the combustion treatment process, and to reduce the processing cost of energy-saving sewage. It is necessary to provide a treated γ stem.

ずlわち、従来、汚泥の脱水lij過工程[Iユ(」・
j(rζζ分合て用いられた口」燃性の炭系紛柁τ、7
つ泥V)発生Wでるる処理時に、流’frVJ床姪体と
してeIh加することV(より、好気性生物融化τ促迅
し、かつ、汚θヒの沈降を速のるとともに、該si″、
、11)汚泥と混合状憑のit脱水P壇し、得られた弱
脱水ケーキの焼却灰化処理を行う一連の操作が円曲とな
り、従来流動床活性汚泥法で問題と妊れていた装置の仮
舖階から、カコ過、焼却へとi&すことにより、生物処
理では能力が安駕し、f’i泥の沈I!ψ分喘性訃よび
浄化能力が向上し、汚泥脱水では、高圧搾、前脱水を可
能化せしめ、自燃性の脱水ケーキを得ることがでさ、脱
水ケーキの焼却では助燃フ11]が必要でなく、焼却灰
が少ない一連の汚水処理システムを提供する事ができた
のである。
Conventionally, the sludge dewatering process [Iyu ('')
j(rζζ) flammable carbonaceous powder τ, 7
Addition of eIh as a flow 'frVJ bed body during treatment of generated W ″,
, 11) The series of operations for dehydrating the sludge and mixed matter and incinerating and ashing the resulting weakly dehydrated cake is circular, and this equipment has been problematic in the conventional fluidized bed activated sludge method. By changing from a temporary floor to filtration and incineration, the ability of biological treatment is lowered and the sedimentation of f'i mud is reduced. ψ The dehydration and purification ability are improved, and in sludge dewatering, high pressure and pre-dehydration are enabled, and a self-combustible dehydrated cake can be obtained, and an auxiliary combustion fan is required for incineration of the dehydrated cake. We were able to provide a series of sewage treatment systems that produce less incinerated ash.

つまり、個々には断片的に知られていた十夾ン一連の汚
水処理システムとして約合化することによっC1これ程
大きな効JAを晃抑することに崩れた特許、昧文はこt
l、までに知らil、ていない。
In other words, the patent collapsed due to the suppression of C1 with such a large effect by combining ten sewage treatment systems, which were individually known in fragments, into a series of sewage treatment systems.
I didn't know until now.

A発明に用いる炭素45f粒Fよ、b’L動脈活性(゛
G泥法での流動媒体、汚犯脱水時力脱水助RIJ及び:
゛指動時の助燃剤としての要素を待つものでなけ几ば7
1らないが、%”!’A J呈の流jiill媒体とし
てVよ、微生物の層床しやすい粉粒でりるとともに、1
1.A気憧内を攪拌するl/(: 、jf)ノこって、
大きな流nW攪攪拌エイヤギ−必要としlい粉粒体でり
る墨が必要で99、さら(lこ、沈降槽で汚泥と均一に
混性された状[株]で、汚泥の沈降分離性を高める粉粒
体であることがl要である。従来、脱水助剤に用いてい
た微粉炭2石炭コークス、石油コークス、亦それ−らの
条件を尚たし、使用可能でbる事を伐々は見い7どした
。特に、石r11]コークスは原油の蒸留による残渣で
、炭素を90滲以上含み、灰分が0.4%以下ときわめ
て低いこと刀)ら、汚泥の脱水、焼却システムで脱水助
剤として添加し、脱水効率を高めるとともに、汚泥焼却
時に助燃剤が必決でなく、また、焼却灰分を少なくでき
るので、最終処分時の妖貸化が可能でのる。また、石油
コークスは扉+1父I戎シナθ・1・よとちず好適で必
っl′こ〇 これらvン炭’rRNイn o、) i> iAl n
’; ji、m ’GCL 7−C,1: ) VC5
脱水助剤としての効果、助燃11111としての7./
l米のうえ、生物処理での効率同上を;3−戊’)−(
i芯台:J’J I’C勘案して設定する必要がめる。
Carbon 45f grains F used in the A invention, b'L arterial activity (Fluid medium in the G mud method, force dehydration aid RIJ during sludge dehydration, and:
゛It is not something that waits for the element as a combustion improver at the time of command.
Although it is not 1, it is %"!'A.
1. I stirred the inside of my mind, l/(: , jf),
A large flow of nW agitation requires 99% of the sludge to be mixed with the sludge in the settling tank, which improves the sedimentation and separation properties of the sludge. It is essential that the material be a granular material that enhances the dehydration aid.Pulverized coal coke, petroleum coke, and petroleum coke that have been conventionally used as dehydration aids can be used by correcting these conditions. In particular, coke is a residue from the distillation of crude oil, contains more than 90% carbon, and has an extremely low ash content of 0.4% or less. It is added as a dehydration aid in the system to increase dewatering efficiency, and since a combustion aid is not necessary when incinerating sludge, and the amount of ash can be reduced, it can be used as a waste at final disposal. In addition, petroleum coke is suitable for door + 1 father I Ekisina θ 1 Yotochi and must be l'ko 〇 these vn coal'rRN in o,) i> iAl n
'; ji, m 'GCL 7-C, 1: ) VC5
7. Effect as dehydration aid, combustion aid 11111. /
In addition to rice, efficiency in biological treatment is the same as above; 3-戊')-(
i-core stand: It is necessary to take J'J I'C into account when setting.

先ず、最初の生物化学的≠→≠処哩。)工・1ンシて」
コ゛いては、炭素粉粒Qλ多い程5.汚泥の沈1・第分
涯1コ1:が良くなるが、多きに過さるとき11、]鳩
t % +VR内の流動 撹 イ半 エ ネ ル ギ 
− が 多 く  な リ 、  1 lこ 、  1
・;シ 素 4分 X’l  I代の点からも不経済で
、す9、足・□j””! Il’j1果よシ、yヶ水の
性多い程その効果も太きいが、余りνC多いとき月r・
P処分に対して、重)政比で30〜1204がが尊しい
First, the first biochemical treatment. )
The more carbon powder particles Qλ, the 5. The settling of sludge in the 1st and 1st minute is improved, but when it is too much, 11,] % + Flow in VR Stirring A Half Energy
- There are many ri, 1 lko, 1
・;Si element 4 minutes Il'j1 fruit, the more yga water, the greater the effect, but if there are too many νC, the moon r.
For P punishment, 30-1204 in the heavy political ratio is the most important.

仄Kid過工程しこpいては、炭素粉粒(457九最〃
:多い程、脱水ケーキの残存水分量が少くなり・がつ、
1戸通、化度も速くなるが、余9に多さ過さ゛る場合V
Cは、d)泥自体の処理iijが低下して多大な脱水設
姉が必要となり、よ1こ、熱エネルギー旧ンこも不経済
で必る。多くの磯性、添加鼠、鑓果1削VCついて実験
を繰送したが、lす(尼の固形分に対してI重量比で3
0〜200%が好ましく、特p(,40〜100%がM
適でめった。
During the Kid's process, carbon powder (4579) was added.
: The higher the amount, the lower the residual moisture content of the dehydrated cake.
If one door is passed, the conversion rate will be faster, but if there are more than 9
C: d) The treatment of the mud itself is degraded, requiring a large amount of dewatering equipment, and the waste of heat energy is also uneconomical. The experiment was repeated with many types of rock, additives, and 1-grain-cut VC;
0 to 200% is preferable, especially p(, 40 to 100% is M
It was suitable and rare.

最後に、脱水ケーキ自体の燃焼性についても多くの実験
を行った。その結果、炭素粉粒の多い程燃焼性は良くな
るが、熱経済的に好ましくない。
Finally, we conducted many experiments on the flammability of the dehydrated cake itself. As a result, the more carbon particles there are, the better the flammability becomes, but it is not thermoeconomically preferable.

また、逆に炭素粉粒が少な過ぎるときは自燃せず、多く
の重油等の助燃剤を要することになる。一般に1.徒も
多く使用さ几ているフィルタープレス型またはベルトプ
レス型脱水機を用いる場合、脱水ケーキ中の残存水分1
d約40〜80%前俵であり、これを自燃させるにrユ
、炭素粉粒が・それを除いた固形分に対して、重量比で
約20〜100%詮まれる必要が必っ〕こ。
On the other hand, if there are too few carbon particles, self-combustion will not occur and a large amount of combustion improver such as heavy oil will be required. Generally 1. When using a filter press type or belt press type dehydrator, which is often used, the residual moisture in the dehydrated cake is 1.
It is about 40 to 80% of the former bale, and in order to make it self-combust, the carbon powder must be about 20 to 100% by weight of the solid content excluding it. child.

こ力、ら生物化学的処理、濾過脱水、焼却の三つの工程
について、奇しくも好適なる石炭粉υj〉加蚕が生物化
学処理よ多発生するij、泥ノ)炭素粉粒を除い/C固
形分に対して、llj 、l4比で30〜1009bの
範囲に収った事は幸いで、りり、木兄uBにががる一連
ノフロセスの成立を町、」目ならしめるものでわるめ 本発明では、前記したように生物化学処理に、流動床媒
体を用いることで汚泥の沈降性が良くなジ、返送汚泥濃
度を高める事ができた。そのために、一般の活性汚泥法
に比べ、1嘘気伶内の戴生物−朋を高く継持する事がロ
ー能となυ、微生物の増加につれて、曝気槽内での酸素
要求償が増えるために、それだけ酸素の供給を増加する
必要がるる。水洗では、酸素源として空気を用いる場合
には下曝気憎への送入量を増加させる事によって対処で
きるが、好ましくは酸素竣度を旨めだ気体・すなわち、
酸素富化空気を送入すれば、液中への溶存酸素量を高め
ることができ、より−1−浄化l:Iヒカを萬め、また
、曝気横内での滞貿時+++1を短、j、ldでさ、装
置を綱車化する事も可能となる。
For the three processes of biochemical treatment, filtration and dehydration, and incineration, coal powder is strangely preferable. On the other hand, it is fortunate that the llj and l4 ratios fell within the range of 30 to 1009b. As mentioned above, by using a fluidized bed medium for biochemical treatment, the sedimentation properties of sludge are improved, and the concentration of returned sludge can be increased. Therefore, compared to the general activated sludge method, it is less able to maintain a high number of microorganisms in one aeration tank, and as the number of microorganisms increases, the oxygen demand in the aeration tank increases. Therefore, the oxygen supply will need to be increased accordingly. In water washing, if air is used as the oxygen source, this can be countered by increasing the amount of air supplied to the lower aeration tank, but it is preferable to use a gas that improves the oxygen level, i.e.,
By introducing oxygen-enriched air, the amount of dissolved oxygen in the liquid can be increased, reducing the -1-purification l:I heat, and also shortening +++1 during aeration. , ld, it is also possible to turn the device into a sheave.

しかしながら、従来、例えば酸素a=ン90%以上に富
化し/こ空気を使用した場合、酸素の利用効率が90〜
95%で、残Vは、酸素を約40〜5096含んだ排ガ
スとして大気に放出していた。
However, conventionally, for example, when using air enriched with oxygen a = 90% or more, the oxygen utilization efficiency was 90~90%.
At 95%, residual V was released into the atmosphere as exhaust gas containing about 40 to 5096 oxygen.

第2番目の発明の目的は、酸素富化空気乞用いた1驕気
イ矯の排ガスを、焼却炉の酸素源に有効利用する事でる
る。
The second object of the invention is to effectively utilize the exhaust gas produced by oxygen-enriched air as an oxygen source for an incinerator.

本発明を図面を参照して詳しく説明すれば、汚水は導管
1で炭素粉粒と連続的または間歇的に混合され、曝気情
3に尋びか1しる。ここに示す汚水上は、下水、し尿、
生活排水、産業排水やrをあらかじめ、生物処理可能な
状態まで処理された有機性汚水をさす。たとえば、下水
の場合VCは、沈砂、スクリーニング、最初沈殿処理さ
れた状態の汚水をさす。なお、この時の炭素粉粒は、I
H接、曝気槽3に添カロ、混合してもきしつかえない事
はい曝して、溶存酸素を供給する。ととも−に、槽内を
撹拌、混合して、好気性に保ち、導入された炭素粉粒に
着床した微生物によつ−C2汚水中の44倣ト〃を分解
し、汚水を浄化する。
To explain the invention in detail with reference to the drawings, sewage is mixed continuously or intermittently with carbon powder in a conduit 1 and subjected to an aeration process 3. The sewage water shown here is sewage, human waste,
It refers to organic wastewater that has been treated in advance to a state where it can be biologically treated, such as domestic wastewater, industrial wastewater, or r. For example, in the case of sewage, VC refers to sewage that has been subjected to sedimentation, screening, and initial settling treatment. In addition, the carbon powder at this time was I
H-contact is applied to the aeration tank 3, and dissolved oxygen is supplied by exposing it to the aeration tank 3 so that it does not become too tight even when mixed. At the same time, the inside of the tank is stirred and mixed to keep it aerobic, and the microorganisms that have settled on the introduced carbon particles decompose the 44 imitated carbon in the C2 sewage and purify the sewage. .

曝気循3で処理された15水は、炭素粉粒を含んだ汚泥
とともしC1沈泥伶ムに々* A −、a h、、面形
′吻を沈降分離する。分陥恢の上澄水は、導音7より処
理水として排出芒ルる。沈降汚泥は、炭素粉粒と混合状
態のまま、一部返送汚泥として1曝気槽3にもど芒れ、
清白の倣生吻鎚娑冒庚度VC釉持する。
The water treated in the aeration cycle 3 is separated by sedimentation into sludge containing carbon particles and C1 silt. The supernatant water from the separation is discharged as treated water through the conductor 7. Some of the settled sludge is returned to the aeration tank 3 as return sludge while remaining mixed with carbon powder.
A pure white imitation with a VC glaze.

一方、残りの汚泥は、余剰汚、泥として骨管8を介・し
て、汚泥貯留情10に導ひかれる。さらに、汚泥は4宥
12で可燃性の高分子凝集剤を添加品会し、脱水機13
に供線さiする。
On the other hand, the remaining sludge is led to the sludge storage chamber 10 via the bone canal 8 as surplus sludge and mud. Furthermore, the sludge was added with a combustible polymer flocculant at 4.12 centimeters, and then added to the dehydrator 13.
The line will be connected to the

この場合の高分子凝集剤の硝7JO−碓rh、汚泥の注
状VCよって左右されるが、汚泥中vJ炭素ω粒以外の
固形公転JΔ゛に対して亜破比で、0.5〜1.5 ;
Il奈加ずれば効率の良い脱水を行う仁とができる。
In this case, it depends on the polymer coagulant 7JO-Rh and the sludge injection shape VC, but the sub-burst ratio is 0.5 to 1 with respect to solid revolution JΔ゛ other than vJ carbon ω grains in the sludge. .5;
If you add water, you will be able to perform efficient dehydration.

脱水機13μ、脱水ケーキの焼却ケ考1可し/こ場合、
フィルタープレスで高圧ジRによる高脱水なイテって、
ケーキ水分が低く、完熱はの商い脱水ケーキを作るのが
好ましいが、ベルトフ”レス式の1反永−磯を用いても
、水分のかなシ低い脱水ケーキとなるため、炭素粉粒の
イ耘加姐の調整によって、十分自ν然性の脱水ケーキを
得ることができる。
Dehydrator 13μ, incineration of dehydrated cake 1 possible/In this case,
Highly dehydrated by high pressure di-R with filter press,
It is preferable to make a dehydrated cake because the cake moisture content is low and it takes a long time to fully heat, but even if you use a belt-free one-pan permanent cake, it will result in a dehydrated cake with a low moisture content. With the adjustment made by Ms. Yuka, a sufficiently natural dehydrated cake can be obtained.

脱水後、脱水jp液ば導管18によって沈殿確6に返え
され、脱水ケーキは焼却炉15に運ばれる。焼却炉15
 VC&j、 導管17より燃焼用空気が送入哀れ、焼
却灰t:iが1.管16より排出略ンL、廃乗処分され
る。あらかじめ、脱水ケーキが自燃性となるように、1
座気(Jhで炭素粉粒を象肌している1こめ11こ、焼
却炉15へ電油等の助熱剤を供給する必要がない。しか
しながら、9“6却f15の点火時には、燃焼募囲気作
υに助燃剤が必要なのは名うまでもない。
After dehydration, the dehydrated cake is returned to the sedimentation chamber 6 via a conduit 18, and the dehydrated cake is transported to an incinerator 15. Incinerator 15
VC & j, combustion air is fed from conduit 17, incineration ash t:i is 1. It is discharged from pipe 16 and disposed of. In advance, so that the dehydrated cake becomes self-combustible,
There is no need to supply a heat aid such as electric oil to the incinerator 15 in the case where the carbon powder is injected into the incinerator 15. However, when igniting the incinerator 15, the combustion It goes without saying that a combustion aid is necessary for enclosing air production υ.

な訃、曝気槽3で酸素を用いた場合の排ガス乞尋肯19
によって、焼却炉15の 導管17に斗びけば、排ガス
中の酸素を燃焼用r)り素として有効利用する事ができ
る。
19. Exhaust gas request when oxygen is used in aeration tank 3
By passing the oxygen into the conduit 17 of the incinerator 15, oxygen in the exhaust gas can be effectively used as phosphorus for combustion.

なお、一般I(下水等の汚水には、イオウ分を含んでい
る場合が多いが、その脱水ケーキを燃焼すると、ゼFガ
ス中にイオウ酸化物が含まれ、大気汚染をきたすためP
C、カルシウムを用いて1ノドガス処琥をする必要がる
る。しかしながら、脱水ケーキ中に消石灰等のカルシウ
ムk lbs加しておけば、ル”6却炉内で0aSO4
となυ、ジ1“ガス中のイオウ酸化物を少lくする供が
できるので、木究明シこ2いても、特に、燃焼ガス中の
弗脈はガスの両度)A制が厳しい場合には、4管12で
凝集剤を添加する前に、予じめ、消石灰’k Mi加m
合し、脱水l焼却を行うこともある。この場合1/Cは
、tri石灰が無機質のために、脱水ケーキの発熱i¥
I:が低下する。そこで、炭素粉粒の添加量を自燃性の
脱水ケーキとなる様に調節すればよい。
In addition, General I (sewage and other sewage often contains sulfur), but when the dehydrated cake is burned, sulfur oxides are included in the ZF gas, causing air pollution.
C. It is necessary to perform one nod gas treatment using calcium. However, if calcium lbs, such as slaked lime, is added to the dehydrated cake, 0aSO4 can be produced in the Le6 incinerator.
It is possible to reduce the amount of sulfur oxides in the gas, so even if the sulfur oxide in the gas is reduced, the sulfur oxide in the combustion gas will be reduced, especially when the A system is strict. In this case, before adding the flocculant in the 4 tube 12, add slaked lime in advance.
In addition, dehydration and incineration may be performed. In this case, 1/C is the heat generation of the dehydrated cake i¥ because the tri lime is inorganic.
I: decreases. Therefore, the amount of carbon powder added may be adjusted so that a self-combustible dehydrated cake is obtained.

一方、下水、し尿、[0ト水の処理で(・、1、木・元
画の生物化学的処理の前後で、汚泥が発生する事がある
が、これらの汚泥と不発明の余剰汚泥をいっしょに、脱
水、焼却しようとする場合には、これらの汚泥を汚泥貯
留相10に導き、混合し−C処理すればよい。しかしな
がら、新規に混合した汚泥に対して、前記した添加率で
もって、炭素粉粒及び凝集剤等を新たに添刀口し、脱水
処理することも口丁能でるる。
On the other hand, sludge may be generated before and after the biochemical treatment of sewage, human waste, and water. If the sludge is to be dehydrated and incinerated at the same time, it is sufficient to introduce these sludges into the sludge storage phase 10, mix them, and perform the -C treatment. It is also possible to newly add carbon powder, flocculant, etc. and perform dehydration treatment.

以上の碌に、本発明は低コストの炭素粉粒を生の向上と
安定化、汚泥の沈降分子’+’lf性の向上及び装置の
簡略化をuJ能とし、汚泥の脱水処理でVよ、新rこに
助剤を冷加する少なく、高圧搾、篩脱水を可り已とし、
さらに、脱水ケーキの焼却において重油等の助燃剤を不
要とし、焼却灰も少なく、さらに、生物化学処理の廃ガ
スな汚泥焼却に有効オリ用でき、全体として処理効≧も
が高< 、矛1&持費の低い、省工坏ルギーの汚水処理
システムとして完成し1このである。
In addition to the above, the present invention uses low-cost carbon powder to improve and stabilize the raw material, improve the '+' lf properties of sludge sediment molecules, and simplify the equipment, and enables V to be used in sludge dewatering treatment. , less cooling of the auxiliary agent, high compression, sieve dehydration possible,
Furthermore, combustion aids such as heavy oil are not required when incinerating dehydrated cakes, and there is little incineration ash.Furthermore, it can be effectively used for incinerating sludge, which is the waste gas of biochemical treatment, and the overall treatment efficiency is high. This is a low-cost, labor-saving sewage treatment system that has been completed.

次に、本9色明の実施例をもとに説明する。Next, an explanation will be given based on an example of the present nine colors.

実施例1 下水処理場の活性汚泥 6000mg/A’  を入れ
た容積500aの自然に返送汚泥できる横這の曝気槽に
、0.05〜Q、 3 rkMの粒径を70%以上含む
万イルコークスを1 ky mえ、B’OD 140 
m g/ eの一次6− g水を280 l / Hr
、空気を1700 l / Hr、オイルコークスに1
日掘り200gの割合で快AnF L、処理水1〆こ汚
泥が冗出しそっし・こなると余老j汚泥とし−CJ外出
した・この栄件で1力月ia] i幀誉し/このち、r
尤I収41′の上泣水はB OD 16〜20 m g
/ A’であッた。また、この時の余剰汚泥の固形分の
うち、それに含まれるオイルコークヌ電ンを除いた頁虚
に対して45%であった。
Example 1 Into a horizontal aeration tank containing 6000 mg/A' of activated sludge from a sewage treatment plant and having a volume of 500 a and capable of naturally returning sludge, ten million coke containing 70% or more of particle sizes of 0.05 to Q, 3 rkM was added. 1 ky me, B'OD 140
m g/e primary 6-g water at 280 l/Hr
, air at 1700 l/Hr, oil coke at 1
At the rate of 200g of daily digging, the treated water is 1〆 and the sludge is flowing out.When it comes to it, I use it as sludge - CJ went out. , r
BOD 16-20 mg
/ It was A'. In addition, the solid content of the excess sludge at this time was 45% of the solid content excluding the oil coke nuden contained therein.

一方、同容積の1体気相・に活性汚泥を同量入れて、オ
イルコークスを加えず、空気を8004/Hr送気し、
同じ一次処理水を加えた場合(ては、BOD 20 m
 g/ 11以丁の処理水を侍る+c n、1351/
Hr9下の一次処理水の供給しか行えなかった。
On the other hand, the same amount of activated sludge was put into the same volume of one-body gas phase, no oil coke was added, and air was blown at 8004/hr.
When the same primary treated water is added (BOD 20 m
g/ 11+ treated water +c n, 1351/
It was only possible to supply primary treated water under 9 hours.

さらに、それぞれの汚泥を10時Ill沈li1 dk
縮後、オイルコークスを除い1こ固形分PC対して)l
オルで1.0%添加撹拌し、ベルトプレス型の脱水試験
機を用いて濾過脱水を行うと、以下の蔓:になった。
Furthermore, each sludge was settled at 10:00.
After shrinkage, excluding oil coke, 1 liter solids per PC)
When 1.0% was added and stirred with a water bottle and filtered and dehydrated using a belt press type dehydration tester, the following vines were obtained.

※印イ倒の1直は、オイルコークスを含んだ1直でりる
*The 1st shift in India is filled with oil coke.

なお、 η Q:乾ケーキ低位発熱量 (kl/kg−DB) d:ケーキ含水比 (kg  Ha 07kg −’ D B )1:蒸発
宿怨 (600td/に9−1420  ) η:焼却炉効率(96) rM m’s床焼却炉をノFJ ’/’ 7e ’−A
 BにpJ、炉効率40〜45ルのため、炉効率40%
として上記式?:満す脱水ケーキは自燃性がある。つま
り、上にCのオ・rルコークスを含ん7ビ余λ、11汚
泥は、助熱J′τりを必要とせず、焼却が【IT ij
f:である。
In addition, η Q: Lower calorific value of dry cake (kl/kg-DB) d: Cake water content ratio (kg Ha 07kg -' DB) 1: Evaporation retention (9-1420 to 600 td/) η: Incinerator efficiency (96 ) rM m's floor incinerator ノFJ '/' 7e '-A
Since pJ is B and furnace efficiency is 40 to 45 l, furnace efficiency is 40%.
As the above formula? : The filled dehydrated cake is self-combustible. In other words, the sludge containing C olefin coke on top of the sludge of 7 B and 11 does not require auxiliary heating and can be incinerated [IT ij
f: is.

実施例2 実施レリ1と同じ1曝気士曹に、活性汚泥を6000m
 g/l入れ、o、 05−’a、 s asの粒(そ
を7096以上含む微粉炭なl +tg加え、下水の一
矢処理水を370/l/Hr、ItDらかしめ、13夕
素f度を30%とした空気を10001 / ur送入
し、微粉炭を1日当υ450gの割合で供給し、1力ツ
4間順養しり(1)ち、BO’D135XQg、/el
ll−次処理水が′Bonxsn+g/4の処理水で得
られた。さらに、この余剰汚泥を10時間濃縮すると、
汚泥濃度が3.4%となった。この汚泥の1fd形分の
うち、それに宮まれる微粉炭、4量はそれ全閉いた重量
に対して89%であった。この娘んされた汚泥の固形分
のうち、それに含°まnる微粉炭MMを除いた型光に対
して、重量比で196の割合でカチオン系高分子凝集剤
を添加撹拌し、フィルタープレスの小試験機で濾過脱水
した結果、乾ケーキ。コ過速度は4.50 icy /
 /に・七。
Example 2 Activated sludge was applied to 6000 m of the same aeration tank as Example 1.
Add g/l, o, 05-'a, sas grains (pulverized coal containing 7096 or more l + tg, add 370/l/Hr of sewage treatment water, ItD harden, 13 yen f degrees) Air with a concentration of 30% was introduced at 10001/ur, pulverized coal was supplied at a rate of υ450g per day, and the temperature was acclimatized for 4 days (1), BO'D135XQg,/el.
ll-sub-treated water was obtained with 'Bonxsn+g/4 of the treated water. Furthermore, if this excess sludge is concentrated for 10 hours,
The sludge concentration was 3.4%. Of the 1 fd of this sludge, the amount of pulverized coal contained in it was 89% of the total weight of the sludge. Of the solid content of this collected sludge, a cationic polymer flocculant was added and stirred at a weight ratio of 196 to the mold light excluding the pulverized coal MM contained therein, and filter press As a result of filtration and dehydration using a small test machine, the result is a dry cake. The overspeed is 4.50 icy/
/ Ni・Seven.

クーキ水分61.3%、乾ケーキ低位発熱f4330 
M / IC9−D Sとなり、実施例1に示した式に
より自燃性があった。
Cake moisture 61.3%, dry cake low heat generation f4330
M/IC9-DS, and was self-combustible according to the formula shown in Example 1.

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

図面は、本発明の汚水の処理ならびにそのlri泥のM
 jN方法の70−シートでるる。 符号説明 1、j、5,7,8.9.11,12.14,15.1
6.17.19   導  管 3 @気Ni    6 沈厳槓 lO汚泥貯留搏    13 脱水機 /、5′″   17
The drawings show the sewage treatment of the present invention and its LRI mud M
70-sheet of jN method. Code explanation 1, j, 5, 7, 8.9.11, 12.14, 15.1
6.17.19 Conduit 3 @Ni 6 1O sludge storage 13 Dehydrator/, 5''' 17

Claims (1)

【特許請求の範囲】 (1+  汚水に、連続的または間歇的に炭素粉粒を加
え、空気または酸素富化空気を用いて、好気的な生物化
学的処理を゛行い、該処aより発生した、炭素粉粒ゲ含
んだ余剰汚泥K、可燃性の凝集剤を添加して一過脱水し
、さらに、該脱水ケーキを焼却する事を特徴とする′°
″ 汚水の処理方法。 (2)  上記炭素粉粒の添加湾を、発生余剰汚泥の固
形分より、炭素粉粒を除いた取部:に対して、炭素粉粒
の電晴が30〜100%となるように加える特許請求の
範囲第+1)項記載の汚水の処理方法。 (3)  上記炭素粉粒を、微粉炭とする特許請求の範
囲#;t11項記載の汚水の処理方法。 (4)  上記炭素粉粒を石炭コークスとする特許請求
の範囲第(1)項記載の汚水の処理方法。 (5)  上記炭素粉粒を石油コークスと1−るjF+
酌Mli求の範囲第(ム)項記載の汚水の処理方法。 (6)す≠→今≠酸素富化空気をIffいて好気的な生
物化学的処理を行った時の含1:iシ素亮ガスを、上記
脱水ケーキを焼ム1jする・烏合σ)久素・原とする特
許請求の範囲力(1)項記載の汚水び)処理方法・
[Scope of Claims] (1+ Carbon powder is added continuously or intermittently to wastewater, and an aerobic biochemical treatment is performed using air or oxygen-enriched air, and the wastewater is generated from the treatment a. The surplus sludge K containing carbon powder is temporarily dehydrated by adding a flammable flocculant, and the dehydrated cake is further incinerated.
``Method for treating sewage. (2) The above carbon powder addition bay is removed from the solid content of generated excess sludge, and the carbon powder is 30 to 100% of the total content of the carbon powder. A method for treating sewage according to Claim No. +1), wherein the carbon powder is pulverized coal. (4) A method for treating sewage according to Claim No. ) The wastewater treatment method according to claim (1), wherein the carbon powder is coal coke. (5) The carbon powder is petroleum coke.
The method for treating sewage as described in item (m) above. (6) So≠→Now≠When oxygen-enriched air is turned on and aerobic biochemical treatment is carried out, the above dehydrated cake is baked with 1:i silicon gas and the above dehydrated cake is heated. The sewage treatment method described in claim (1) to Hisa and Hara.
JP58082300A 1983-05-11 1983-05-11 Filthy water disposal Pending JPS59209699A (en)

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Application Number Priority Date Filing Date Title
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JPS59209699A true JPS59209699A (en) 1984-11-28

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JP58082300A Pending JPS59209699A (en) 1983-05-11 1983-05-11 Filthy water disposal

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108751583A (en) * 2017-10-13 2018-11-06 林翔 A kind of high-efficiency environment friendly sewage purifier
CN114524583A (en) * 2022-02-08 2022-05-24 海南大学 High-efficiency environment-friendly sewage treatment method

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5436062A (en) * 1977-08-24 1979-03-16 Niigata Eng Co Ltd Method of treating gas liquor

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5436062A (en) * 1977-08-24 1979-03-16 Niigata Eng Co Ltd Method of treating gas liquor

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108751583A (en) * 2017-10-13 2018-11-06 林翔 A kind of high-efficiency environment friendly sewage purifier
CN114524583A (en) * 2022-02-08 2022-05-24 海南大学 High-efficiency environment-friendly sewage treatment method

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