JPS61129097A - Treatment of sludge - Google Patents
Treatment of sludgeInfo
- Publication number
- JPS61129097A JPS61129097A JP24874284A JP24874284A JPS61129097A JP S61129097 A JPS61129097 A JP S61129097A JP 24874284 A JP24874284 A JP 24874284A JP 24874284 A JP24874284 A JP 24874284A JP S61129097 A JPS61129097 A JP S61129097A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- washing
- water
- equipment
- 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
Links
Landscapes
- Treatment Of Sludge (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は廃水処理により排出される汚泥の処理法に関し
、特に汚泥中のCt−濃度を低減させる汚泥の処理方法
に関する。DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to a method for treating sludge discharged from wastewater treatment, and particularly to a method for treating sludge that reduces the Ct concentration in the sludge.
(従来の技術)
廃水処理設備から排出される汚泥は焼却炉で焼却され無
害化される場合が多い。一方し尿等の廃水中には、塩素
イオン(aZ−)が含ま、れているため排出される汚泥
もCl−(一般的に、シ永中のOZ−は2000〜50
00ダ/l程度)を含んでいる。このOZ−を含んだ汚
泥を焼却すると焼却炉内でHOjが生成され、排ガスと
なって大気へ放出されている。(Prior Art) Sludge discharged from wastewater treatment equipment is often incinerated in an incinerator to render it harmless. On the other hand, wastewater such as night soil contains chlorine ions (aZ-), so the sludge discharged also has Cl-
00 da/l). When this OZ-containing sludge is incinerated, HOj is generated in the incinerator and is released into the atmosphere as exhaust gas.
大気汚染防止法ではこの□ような焼却施設から排出され
るHOjの濃度を450 ppm以下にすることが決め
られておシ、この値を守るために従来から次の方法が行
なわれている。The Air Pollution Control Law stipulates that the concentration of HOj discharged from such incineration facilities must be below 450 ppm, and the following methods have been used to maintain this value.
(1)汚泥の焼却前に汚泥中に石灰を混入し生成したH
Ojを石灰で反応吸収し除去する方法(第3図参照)
(2) 汚泥焼却排ガス中に石灰を噴霧し、HOjを
反応吸収し除去する方法 (第4図参照)(3) 排
ガスをアルカリ(例えばMaxiり溶液等で洗浄しHo
tを反応吸収し除去する方法 (第5図参照)
(4)原廃水を希釈し、排出される汚泥中に含まれるo
r−濃度を低減して焼却する方法 (第6図参照)
(5)汚泥を洗浄しO2−濃度を低減してから焼却する
方法 (第7図参照)
上記第3図〜第7図において、1は廃水、2は廃水処理
装置、3は処理水、4は余剰汚泥、5は汚泥濃縮装置、
6は濃縮汚泥、7は石灰、8は汚泥脱水機、9は脱水汚
泥、10は汚泥焼却装置、11は焼却廃ガス、12は灰
回収設備、13は排ガス、14はアルカIJI、15は
ガス洗浄装置、16はガス洗浄廃液、17は希釈水、1
8は汚泥洗浄水、j?ij:洗浄槽、20は洗浄廃液で
ある。(1) H generated by mixing lime into sludge before incineration
A method of removing Oj by reaction absorption with lime (see Figure 3) (2) A method of spraying lime into sludge incineration exhaust gas and reacting and absorbing HOj and removing it (see Figure 4) (3) A method of converting exhaust gas into alkali (see Figure 4) For example, wash with Maxi solution etc.
(See Figure 5) (4) Dilute the raw wastewater to remove the o contained in the discharged sludge.
A method of incinerating after reducing the r-concentration (see Figure 6) (5) A method of incinerating after washing the sludge and reducing the O2- concentration (see Figure 7) In Figures 3 to 7 above, 1 is wastewater, 2 is wastewater treatment equipment, 3 is treated water, 4 is surplus sludge, 5 is sludge thickening equipment,
6 is thickened sludge, 7 is lime, 8 is sludge dehydrator, 9 is dehydrated sludge, 10 is sludge incinerator, 11 is incineration waste gas, 12 is ash recovery equipment, 13 is exhaust gas, 14 is Alka IJI, 15 is gas Cleaning equipment, 16 gas cleaning waste liquid, 17 dilution water, 1
8 is sludge washing water, j? ij: washing tank; 20 is washing waste liquid;
上記のうち(1) 、 (2) 、 (3)については
石灰やNaOH等の薬品を必要とし更に(1) 、 (
2) Kついては飛散した石灰の回収設備、(3)につ
いては洗浄排液の処理を必要としていた。また(4)
、 (5J Kついても多量の希釈水や洗浄水が必要で
あシ、これが廃水処理設備を犬きくする原因にもなって
いる。Of the above, (1), (2), and (3) require chemicals such as lime and NaOH;
2) For K, equipment was required to recover scattered lime, and for (3), treatment of cleaning waste liquid was required. Also (4)
(Even with 5JK, large amounts of dilution water and washing water are required, which is also a cause of strain on wastewater treatment equipment.
(発明が解決しようとする問題点)
本発明は上記従来法のような欠点のない汚泥中のCl−
濃度を低減する方法、特に、上記(5)に着目し、汚泥
の洗浄水を節水できる方法を提供しようとするものであ
る。(Problems to be Solved by the Invention) The present invention solves the problem of Cl-
The present invention aims to provide a method of reducing the concentration, particularly focusing on the above (5), and a method of saving water for washing sludge.
(問題点を解決するための手段)
すなわち、本発明は廃水処理によって排水される汚泥を
焼却する前に、汚泥の脱水操作時に生ずる炉布洗浄水な
どの機器洗浄廃水や処理設備で用いた雑水などにより汚
泥を洗浄して汚泥中のOl−濃度を低減させることを特
徴とする汚泥処理法である。(Means for Solving the Problems) That is, the present invention uses equipment cleaning wastewater such as furnace cloth cleaning water generated during sludge dewatering operation and miscellaneous wastewater used in treatment equipment before incinerating sludge discharged from wastewater treatment. This is a sludge treatment method characterized by washing the sludge with water or the like to reduce the Ol- concentration in the sludge.
通常、廃水処理設備から排出される汚泥は脱水工程にお
いて含水率を低下させてから焼却される。この脱水工程
には遠心分離機やベルトプレス、フィルタプレス等が用
いられている。これら脱水機には必らずヂ布洗浄水等の
機器洗浄水が必要であシ、この洗浄水としては井戸水や
工業用水等、O/−濃度が低い水が用いられている。こ
の洗浄水は従来、廃水処理工程へ移送され処理された後
に放流されていた。Usually, sludge discharged from wastewater treatment equipment is incinerated after its moisture content is reduced in a dewatering process. A centrifugal separator, belt press, filter press, etc. are used in this dehydration process. These dehydrators necessarily require equipment washing water such as cloth washing water, and water with a low O/- concentration, such as well water or industrial water, is used as this washing water. Conventionally, this wash water was transferred to a wastewater treatment process, treated, and then discharged.
本発明はこのar−濃度の低い水を廃水処理工程へ移送
する前に1汚泥洗浄水として再利用し、汚泥に含まれる
Cl−濃度を低減させ、汚泥焼却炉から排出されるFi
CJl 9度を低減することを特徴とするものである。The present invention reuses this water with low ar- concentration as sludge washing water before transferring it to the wastewater treatment process, reduces the Cl- concentration contained in the sludge, and reduces the Fi-concentration discharged from the sludge incinerator.
It is characterized by reducing CJl 9 degrees.
本発明は従来そのまま廃水処理工程に送られてすてられ
ていた(!/−濃度の低い水を再利用するため特に、H
(3/i度低減のために薬品や、新しい洗浄水を必要と
せず、経済的な汚泥処理方法である。Conventionally, the present invention was directly sent to the wastewater treatment process and wasted (!/- In order to reuse water with a low concentration, H
(3/i It is an economical sludge treatment method that does not require chemicals or new washing water to reduce degrees.
本発明は前記(5)の方法(第7図)のaCt低減法を
改良した方法である。今、こ\に第7図の方法の装置を
機器洗浄水をも含めて詳細に示す第2図と、本発明方法
の一実施態様を示す第1図とを対比して、本発明を詳述
する。The present invention is an improved aCt reduction method of method (5) (FIG. 7). The present invention will now be explained in detail by comparing FIG. 2, which shows the apparatus of the method of FIG. 7 in detail, including equipment washing water, with FIG. 1, which shows an embodiment of the method of the present invention. Describe.
第1図、第2図において、1は廃水、2は廃水処理装置
、3は処理水、4は余剰汚泥、5は洗浄槽、6は洗浄汚
泥、7は汚泥濃縮槽、8は濃縮汚泥、9は汚泥脱水機、
10は脱水汚泥、11は汚泥焼却装置、12は排ガス、
13は汚泥洗浄水、14は機器洗浄水、15は機器洗浄
廃水、16は汚泥洗浄廃水である。1 and 2, 1 is wastewater, 2 is wastewater treatment equipment, 3 is treated water, 4 is excess sludge, 5 is a washing tank, 6 is washed sludge, 7 is a sludge thickening tank, 8 is thickened sludge, 9 is a sludge dehydrator,
10 is dehydrated sludge, 11 is a sludge incinerator, 12 is exhaust gas,
13 is sludge washing water, 14 is equipment washing water, 15 is equipment washing wastewater, and 16 is sludge washing wastewater.
第1図において、廃水1は廃水処理装置2で処理され、
処理水3と余剰汚泥4に分離される。In FIG. 1, wastewater 1 is treated in a wastewater treatment device 2,
Separated into treated water 3 and surplus sludge 4.
余剰汚泥4は洗浄槽5において後述の機器洗浄廃水15
により洗浄され、汚泥に含まれるOl−分が低減される
。洗浄汚泥6は汚泥濃縮槽7で濃縮され、汚泥洗浄廃水
16と!I縮汚泥8に分離される。汚泥洗浄廃水16は
廃水処理装置2に送シ処理され、濃縮汚泥8は汚泥脱水
機9により脱水され脱水汚泥10となる。汚泥脱水機9
は機器洗浄水14で洗浄されるが、その機器洗浄廃水1
5は前述したように汚泥洗浄水13として再利用され、
洗浄槽5へ送られる。脱水汚泥10は汚泥焼却装置11
で焼却され、排ガス12が排出される。Excess sludge 4 is sent to the cleaning tank 5 as equipment cleaning wastewater 15, which will be described later.
The sludge is washed and the Ol- content contained in the sludge is reduced. The washed sludge 6 is concentrated in the sludge thickening tank 7 and becomes sludge washing wastewater 16! It is separated into reduced sludge 8. The sludge cleaning wastewater 16 is sent to the wastewater treatment device 2 for treatment, and the concentrated sludge 8 is dehydrated by the sludge dehydrator 9 to become dehydrated sludge 10. Sludge dehydrator 9
is washed with equipment washing water 14, but the equipment washing waste water 1
5 is reused as sludge washing water 13 as mentioned above,
It is sent to the cleaning tank 5. Dehydrated sludge 10 is transferred to sludge incinerator 11
The waste gas 12 is incinerated and the exhaust gas 12 is discharged.
機器洗浄水は通常O2−濃度の低い井水や工水等が用い
られており機器洗浄廃水中のCt−濃度も低い。従来こ
の機器洗浄廃水はそのまま廃水処理設備に送られていた
が、本発明においてはこの機器洗浄廃水を汚泥洗浄水と
して再利用するため洗浄槽へ送っている。機器洗浄廃水
中のCl−濃度は低いため余剰汚泥のaZ−が洗浄希釈
され余剰汚泥のCl−濃度が低下する。このため汚泥を
濃縮、脱水後に焼却しても排ガス中のHot濃度が低減
される。Equipment cleaning water is usually well water or industrial water with a low O2 concentration, and the Ct concentration in the equipment cleaning wastewater is also low. Conventionally, this equipment washing wastewater was sent as is to a wastewater treatment facility, but in the present invention, this equipment washing wastewater is sent to a washing tank for reuse as sludge washing water. Since the Cl- concentration in equipment washing wastewater is low, aZ- in the excess sludge is washed and diluted, and the Cl- concentration in the excess sludge decreases. Therefore, even if the sludge is incinerated after being concentrated and dehydrated, the hot concentration in the exhaust gas is reduced.
これに対して、第2図の方法は、汚泥洗浄水13と機器
洗浄水14の2ケ所に各々別に洗浄用水を用いていた点
にある。これに対して本発明罠おいては機器洗浄水を汚
泥洗浄水に再利用するため、洗浄用水(通常は井水又は
工水)が約4に節減できる特徴がある。またこれら洗浄
廃水は従来、廃水処理設備へ送られ処理されていたが、
これら洗浄廃水の量は原廃水量の2〜3倍にも及ぶこと
があり、洗浄廃水量が約/に節減されれば廃水処理設備
の容量の低減も可能となる。In contrast, the method shown in FIG. 2 uses separate cleaning water at two locations: sludge cleaning water 13 and equipment cleaning water 14. On the other hand, in the trap of the present invention, since equipment washing water is reused as sludge washing water, the amount of washing water (usually well water or industrial water) can be reduced to about 4 times. Additionally, these cleaning wastewaters were conventionally sent to wastewater treatment facilities for treatment;
The amount of these washing wastewaters can be as much as 2 to 3 times the amount of raw wastewater, and if the amount of washing wastewaters can be reduced to about 1/2, it is also possible to reduce the capacity of wastewater treatment equipment.
第1図は本発明の一実施態様のフローを示し、s2図〜
第7図は従来の汚泥中のOl−濃度を低減させる方法の
フローを示す。
復代理人 内 1) 明
復代理人 萩 原 亮 −
第6図 第7図Fig. 1 shows the flow of one embodiment of the present invention, and Fig. s2~
FIG. 7 shows the flow of a conventional method for reducing the Ol concentration in sludge. Sub-Agent 1) Meifu Agent Ryo Hagiwara - Figure 6 Figure 7
Claims (1)
の脱水操作時に生ずるろ布洗浄水などの機器洗浄廃水や
処理設備で用いた雑水などにより汚泥を洗浄して汚泥中
のCl^−濃度を低減させることを特徴とする汚泥処理
法。Before incinerating the sludge discharged during wastewater treatment, the sludge is washed with equipment cleaning wastewater such as filter cloth washing water generated during sludge dehydration, gray water used in treatment equipment, etc. to remove Cl^ in the sludge. - A sludge treatment method characterized by reducing the concentration.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP24874284A JPS61129097A (en) | 1984-11-27 | 1984-11-27 | Treatment of sludge |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP24874284A JPS61129097A (en) | 1984-11-27 | 1984-11-27 | Treatment of sludge |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS61129097A true JPS61129097A (en) | 1986-06-17 |
Family
ID=17182684
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP24874284A Pending JPS61129097A (en) | 1984-11-27 | 1984-11-27 | Treatment of sludge |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS61129097A (en) |
-
1984
- 1984-11-27 JP JP24874284A patent/JPS61129097A/en active Pending
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