JPS61268400A - Method for modifying sludge for dehydration - Google Patents
Method for modifying sludge for dehydrationInfo
- Publication number
- JPS61268400A JPS61268400A JP60109651A JP10965185A JPS61268400A JP S61268400 A JPS61268400 A JP S61268400A JP 60109651 A JP60109651 A JP 60109651A JP 10965185 A JP10965185 A JP 10965185A JP S61268400 A JPS61268400 A JP S61268400A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- fibrous substance
- digestion
- added
- raw
- 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
- 239000010802 sludge Substances 0.000 title claims abstract description 65
- 238000000034 method Methods 0.000 title claims abstract description 14
- 230000018044 dehydration Effects 0.000 title abstract description 9
- 238000006297 dehydration reaction Methods 0.000 title abstract description 9
- 239000000126 substance Substances 0.000 claims abstract description 21
- 239000010801 sewage sludge Substances 0.000 claims description 3
- 238000002715 modification method Methods 0.000 claims 1
- 230000029087 digestion Effects 0.000 abstract description 8
- 239000004744 fabric Substances 0.000 abstract description 4
- 238000000926 separation method Methods 0.000 abstract description 4
- 238000004062 sedimentation Methods 0.000 abstract 2
- 239000007787 solid Substances 0.000 description 9
- 230000000694 effects Effects 0.000 description 7
- 239000002657 fibrous material Substances 0.000 description 7
- 235000019750 Crude protein Nutrition 0.000 description 2
- 239000000654 additive Substances 0.000 description 2
- 230000000996 additive effect Effects 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 230000002747 voluntary effect Effects 0.000 description 2
- 125000000129 anionic group Chemical group 0.000 description 1
- 125000002091 cationic group Chemical group 0.000 description 1
- 229920006317 cationic polymer Polymers 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 125000005397 methacrylic acid ester group Chemical group 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 229920000620 organic polymer Polymers 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 238000002407 reforming Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 230000008719 thickening Effects 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
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、下水汚泥を効果的に脱水するための脱水用汚
泥の改質方法に関する。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for reforming dewatering sludge for effectively dewatering sewage sludge.
ベルトプレス型脱水機は、通常、下水汚泥の種類や、濃
度、有機分などの性状により、ケーキ水分、沢過速度、
剥離性々どの脱水性能が異なる。Belt press type dewatering machines normally have different levels of cake moisture, slush overspeed,
The dehydration performance differs depending on the peelability.
下水汚泥の種類は一般に、最初沈殿池から発生する生汚
泥、最終沈殿池から発生する余剰活性汚泥、および消化
槽からの引抜き消化汚泥等に区分さnる0このうち消化
汚泥は、消化過程において、有機分の分解、粒子の微細
化等により、繊維状物質が消化槽投入前の生汚泥に比べ
減少する。Types of sewage sludge are generally divided into raw sludge generated from the initial settling tank, surplus activated sludge generated from the final settling tank, and digested sludge drawn from the digestion tank. Due to the decomposition of organic matter and the miniaturization of particles, the amount of fibrous material is reduced compared to the raw sludge before being put into the digester.
繊維状物質は、一般にベルトプレス型脱水機の脱水性能
に影響が大きく、繊維状物質の少ない前記の消化汚泥は
、生汚泥に比べると、脱水性能が劣る場合も少なくない
。Fibrous substances generally have a large effect on the dewatering performance of a belt press type dehydrator, and the above-mentioned digested sludge, which has a small amount of fibrous substances, often has inferior dewatering performance compared to raw sludge.
また、余剰活性汚泥は、有機分が多く、繊維状物質が少
ないため、単独で脱水することは困難なのが通例である
。In addition, surplus activated sludge has a large amount of organic content and a small amount of fibrous substances, so it is usually difficult to dehydrate it alone.
こうした難脱水性の消化汚泥脱水や余剰活性汚泥を単独
で脱水する場合、従来は、凝集剤の添加率の増加や処理
量の減少等で対処したり、カチオン性とアニオン性の2
種類の凝集剤を併用して脱水性能を維持する方法を採用
するなどの対処をしている。When dewatering digested sludge or surplus activated sludge, which is difficult to dewater, conventionally, measures were taken by increasing the addition rate of flocculant or reducing the amount of treatment, or by using cationic and anionic sludge.
Measures are being taken to maintain dehydration performance by using different types of flocculants.
他方で、カチオン性高分子凝集剤とパルプを混合し、汚
泥に添加する方法などの例も知らnている(特開昭59
−87097号公報)。On the other hand, there is also an example of a method in which a cationic polymer flocculant and pulp are mixed and added to sludge (Japanese Patent Application Laid-open No. 59-1999).
-87097).
しかし、こうした方法では、いづnも凝集剤を系外から
得るため、ランニングコストの増大を招き、得策とはい
えない0
本発明は、上記従来の問題点を解消し、凝集剤に代表さ
nるランニングコストヲ増大させることなく、脱水性能
を著しく向上させる方法を提供するものである。However, in such a method, the flocculant is obtained from outside the system, which increases running costs and is not a good idea.The present invention solves the above-mentioned conventional problems. The present invention provides a method for significantly improving dewatering performance without increasing running costs.
本発明者らは、脱水性能に影響の大きい繊維状物質が生
汚泥中に多く存在することに着目し、生汚泥から分離回
収した繊維状物質を前記の難脱水性の消化汚泥や、余剰
活性汚泥に添加す扛ば、ベルトプレス型脱水機の脱水性
能を著しく向上させることができることを知見した0
すなわち、本発明は、下水汚泥の脱水処理に際し、汚泥
処理プロセスの最初沈殿池から発生する生汚泥中の繊維
状物質を分離回収し、余剰活性汚泥または消化汚泥に添
加することを特徴とするものである。The present inventors focused on the fact that raw sludge contains many fibrous substances that have a large effect on dewatering performance. It has been found that the dewatering performance of a belt press type dewatering machine can be significantly improved by adding it to sludge. This method is characterized by separating and recovering fibrous substances in sludge and adding them to surplus activated sludge or digested sludge.
本発明では、生汚泥中の繊維状物質を分離回収し、こn
を余剰活性汚泥または消化汚泥に添加している。したが
って、そ扛ら汚泥には繊維分が添加されるので、良好な
脱水性能を示す〇〔発明の具体例〕
以下本発明をさらに詳説する。In the present invention, fibrous substances in raw sludge are separated and recovered.
is added to surplus activated sludge or digested sludge. Therefore, since a fiber component is added to the sludge, it exhibits good dewatering performance. [Specific Examples of the Invention] The present invention will be explained in more detail below.
第1図は本発明法を含む汚泥処理工程を示したもので、
流入下水1は沈砂池2に流入さn。Figure 1 shows the sludge treatment process including the method of the present invention.
The inflowing sewage 1 flows into the settling basin 2.
ここにおいて粗粒分が沈降さfL*後、最初沈殿池3に
導かnた後、エアレーションタンク4および最終沈殿池
5を経て、清浄化さnた後、放流さfる。Here, after the coarse particles are settled fL*, they are first led to a settling tank 3, then passed through an aeration tank 4 and a final settling tank 5, where they are cleaned and then discharged.
最終沈殿池5からの余剰活性汚泥6A、6Bは最初沈殿
池3およびエアレーションタンク4に返送さnる〇
一方で、本発明では、最初沈殿池3における、好ましく
は濃縮槽7を通した生汚泥8からは、繊維状物質分離装
置9、たとえばスクリーンまたは振動ふるい等によって
、繊維状物質10を分離する。分離後の汚泥11は消化
槽12において消化汚泥13とし、この消化汚泥13に
対して混合機14により繊維状物質10と混合し、この
繊維状物質添加余剰汚泥15をベルトプレス型脱水機1
6にかけ、脱水を図る。17は脱水ケーキである。Surplus activated sludge 6A, 6B from the final settling tank 5 is returned to the first settling tank 3 and the aeration tank 4. On the other hand, in the present invention, the surplus activated sludge is returned to the first settling tank 3, preferably through the thickening tank 7. Fibrous substances 10 are separated from the sludge 8 by a fibrous substance separator 9, such as a screen or vibrating sieve. The sludge 11 after separation is made into digested sludge 13 in a digestion tank 12, this digested sludge 13 is mixed with fibrous material 10 in a mixer 14, and this fibrous material-added surplus sludge 15 is transferred to a belt press type dehydrator 1.
6 to dehydrate. 17 is a dehydrated cake.
他方で、繊維状物質lOは、混合機18において、余剰
活性汚泥6C;ンま・た社強制濃縮した余剰活性汚泥と
混合し、繊維状物質添加余剰汚泥19として、脱水機1
6にかけ、脱水を図るようにしてもよい。On the other hand, the fibrous material 10 is mixed in the mixer 18 with surplus activated sludge 6C;
6 for dehydration.
なお、消化汚泥と余剰活性汚泥との両者に対して、繊維
状物質を添加して脱水を図ることも本発明の要旨内であ
る。It is also within the scope of the present invention to add a fibrous substance to both the digested sludge and surplus activated sludge for dewatering.
ところで、分離回収した繊維状物質は、できる限り、水
分を除いた状態で添加し、添加後はよく撹拌し、汚泥中
に分散する必要がある。添加の時期は、有機高分子凝集
剤を汚泥に添加し、凝集フロックを形成させる前に汚泥
に添加混合するのがよく、凝集フロックを形成した後は
効果が少い。By the way, it is necessary to add the separated and recovered fibrous substances in a state in which water is removed as much as possible, and after addition, it is necessary to thoroughly stir the fibrous substances and disperse them in the sludge. As for the timing of addition, it is best to add the organic polymer flocculant to the sludge and mix it with the sludge before forming coagulated flocs, and the effect will be less after the flocs are formed.
添加量としては、添加量が多いほど脱水性能が向上する
が、極端に添加するのは効率的ではなく、したがって、
通常、消化汚泥または余剰活性汚泥の繊維状物質の2〜
4重量倍が好ましいO
〔実施例〕
次に実施例をもって本発明の効果を明らかにする0
なお、以下の実施例においては、繊維状物質を、100
メツシユまたは80メツシユのふるいで分離しうる粗浮
遊物質として定義し、この粗浮遊物質は汚泥中固形物量
に対する比率で表わしたものをペースに添加の比率を設
定したO(実施例1)
固形物濃度3.4係、有機分53.84%、粗浮遊物4
.78%、粗タンパク質24.78%の消化汚泥に、添
加後の粗浮遊物濃度が2; 3,4倍となるように生汚
泥中の100メツシュ粗浮遊物を回転数150 rpm
で撹拌しながら添加し、全固形物が1過面積100i当
518.1gとなる量にする0同回転数に維持したまま
メタクリル酸エステル系4駁塩ポリマを固形物に対し1
係注入し、90秒間凝集させる。次いでr過面積100
dのf布上で120秒間重力沢過1、さらに120秒間
荷重0.02 kg/CI?Lとなるよう予備加圧した
。予備加圧後のケーキの上に、先の1布と同じものを重
ね方晶機械社製テーブルテスタにて脱水テストヲ行った
。As for the amount added, the dehydration performance improves as the amount added increases, but adding too much is not efficient, so
Usually, the fibrous material of digested sludge or surplus activated sludge is
4 times the weight is preferable [Example] Next, the effects of the present invention will be clarified with examples 0 In the following examples, the fibrous material is
It is defined as coarse suspended solids that can be separated with a mesh or 80 mesh sieve, and the addition ratio was set based on the ratio of this coarse suspended solid to the amount of solids in the sludge (Example 1) Solids concentration Section 3.4, organic content 53.84%, crude suspended matter 4
.. 78% crude protein and 24.78% crude protein, 100 mesh coarse suspended matter in raw sludge was added to the digested sludge at a rotation speed of 150 rpm so that the concentration of crude suspended matter after addition was 2 to 3 to 4 times.
While stirring, add the methacrylic acid ester-based 4-metal salt polymer to the solids in an amount that makes the total solids 518.1 g per 100i of molten area while maintaining the same rotation speed.
Inject and allow to flocculate for 90 seconds. Then r over area 100
Gravity flow 1 on the f cloth of d for 120 seconds, and a load of 0.02 kg/CI for another 120 seconds? Preliminary pressure was applied so that the pressure was L. The same fabric as the previous one was placed on top of the pre-pressurized cake, and a dehydration test was conducted using a table tester manufactured by Lapisho Kikai Co., Ltd.
測定した項目は、重力1過ケーキ水分、脱水ケーキ水分
、脱水ケーキ広がり等について測定した。テスト結果は
第1表の通りであった〇第 1 表
注1)添加物は100メツシユ粗浮遊物である0
注2)ケーキ広がりの面積倍率は100cr1.に。Items measured included cake moisture per gravity, dehydrated cake moisture, and dehydrated cake spread. The test results were as shown in Table 1.Table 1 Note 1) The additive was 100 mesh coarse suspended matter.Note 2) The area magnification of the cake spread was 100cr1. To.
対する倍率を示す0
(実施例2)
固形物濃度2.96係、有機分53.55%、粗浮遊物
4.15%、粗タンノくり質23.4−2%の消化汚泥
に、実施例1の100メツシユ粗浮遊物の代わりに、8
0メツシユ粗浮遊物を消化汚泥の粗浮遊物濃度の3,4
倍となるように添加し、他は実施例1と同様に脱水テス
トヲ行った0結果は第2表の通りであり、100メツシ
ユと同程度の効果がみらnた〇
第 2 表
注3)添加物は80メツシユ粗浮遊物を供したO
(考察)
上記実施例によnば、第1および第2表のように、生汚
泥中の繊維状物質を添加することによって、脱水性が向
上することが判る0〔発明の効果〕
以上の通り、本発明によnば、生汚泥から分離回収した
繊維状物質を余剰活性汚泥または消化汚泥に添加するも
のであるから、脱水性能が向上し、たとえば従来法と比
較して、脱水ケーキ水分が約5係低減し、重力1過ケー
キ水分が約2φ低減するとともに、1布との剥離性が向
上するなどの利点かもたらさnる。0 (Example 2) Example 2: Digested sludge with a solid concentration of 2.96%, an organic content of 53.55%, a crude suspended matter of 4.15%, and a crude tanno-crystalline substance of 23.4-2%. Instead of 100 mesh coarse floating matter of 1, 8
0 mesh coarse suspended solids are digested sludge coarse suspended solids concentration 3,4
The dehydration test was carried out in the same manner as in Example 1.The results are shown in Table 2, and the same effect as 100 mesh was observed.Table 2 Note 3) The additive provided 80 mesh of coarse suspended matter. (Discussion) According to the above examples, as shown in Tables 1 and 2, the dewatering performance was improved by adding fibrous substances in raw sludge. [Effect of the Invention] As described above, according to the present invention, since the fibrous material separated and recovered from raw sludge is added to excess activated sludge or digested sludge, the dewatering performance is improved. For example, compared to the conventional method, the dehydrated cake moisture is reduced by about 5 factors, the cake moisture per gravitational force is reduced by about 2φ, and the releasability from cloth is improved.
第1図は本発明法に係る下水処理のブロック図である。
3・・最初沈殿池 5・・最終沈殿池6A〜6C・・
余剰活性汚泥 8・・生汚泥9・・分離装置 10
・・繊維状物質12・・消化槽 13・・消化汚泥
16・・脱水機
手続補正書(自発)
昭和60年7月 5日
昭和60年 特許願 第109651号2 発明の名称
脱水用汚泥の改質方法
3 補正をする者
事件との関係 特許出願人
4 代理人 〒101
5 補正命令の日付 自発補正
6 補正の対象
図面
7 補正の内容FIG. 1 is a block diagram of sewage treatment according to the method of the present invention. 3. Initial settling tank 5. Final settling tank 6A to 6C...
Surplus activated sludge 8. Raw sludge 9. Separation device 10
... Fibrous material 12 ... Digestion tank 13 ... Digested sludge 16 ... Dehydrator procedure amendment (voluntary) July 5, 1985 Patent application No. 109651 No. 109651 2 Title of invention Improvement of sludge for dewatering Quality method 3 Relationship between the person making the amendment and the case Patent applicant 4 Agent 〒101 5 Date of amendment order Voluntary amendment 6 Drawing to be amended 7 Contents of amendment
Claims (1)
最初沈殿池から発生する生汚泥中の繊維状物質を分離回
収し、余剰活性汚泥または消化汚泥に添加することを特
徴とする脱水用汚泥の改質方法。(1) When dewatering sewage sludge, fibrous substances in raw sludge generated from the initial settling tank of the sludge treatment process are separated and recovered, and added to surplus activated sludge or digested sludge. Modification method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60109651A JPS61268400A (en) | 1985-05-22 | 1985-05-22 | Method for modifying sludge for dehydration |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60109651A JPS61268400A (en) | 1985-05-22 | 1985-05-22 | Method for modifying sludge for dehydration |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPS61268400A true JPS61268400A (en) | 1986-11-27 |
Family
ID=14515687
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60109651A Pending JPS61268400A (en) | 1985-05-22 | 1985-05-22 | Method for modifying sludge for dehydration |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61268400A (en) |
Cited By (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2010137158A (en) * | 2008-12-11 | 2010-06-24 | Kubota Kankyo Service Kk | Apparatus for measuring fiber concentration in sludge, apparatus for adjusting fiber concentration in sludge, dehydration equipment and dehydration method |
| CN101767922B (en) | 2010-01-21 | 2012-07-04 | 上海亚同环保实业股份有限公司 | Sludge dehydration treatment technology |
| JP2013119081A (en) * | 2011-12-09 | 2013-06-17 | Kobelco Eco-Solutions Co Ltd | Treatment method and treatment apparatus for phosphorus-containing wastewater |
| WO2015012039A1 (en) | 2013-07-26 | 2015-01-29 | 株式会社石垣 | Recovery device and recovery method for recovering specific material from sludge, sludge dehydration system, and sludge dehydration method |
| JP2015024371A (en) * | 2013-07-26 | 2015-02-05 | 株式会社石垣 | Extraction equipment |
| JP2015054287A (en) * | 2013-09-12 | 2015-03-23 | 株式会社石垣 | Sludge treatment method |
| JP2015054286A (en) * | 2013-09-12 | 2015-03-23 | 株式会社石垣 | Method and system for dewatering sewage sludge |
| JP2016190190A (en) * | 2015-03-31 | 2016-11-10 | 株式会社石垣 | Sludge treatment system and sludge treatment method |
| JP2016190188A (en) * | 2015-03-31 | 2016-11-10 | 株式会社石垣 | Sludge dewatering device and sludge dewatering method |
| JP2017100130A (en) * | 2011-04-26 | 2017-06-08 | 水ing株式会社 | Anaerobic digestion treatment method and anaerobic digestion treatment device |
| JP2018009911A (en) * | 2016-07-15 | 2018-01-18 | 株式会社石垣 | Rotary fiber density meter and method for mud dehydration, using the rotary fiber density meter |
| JP2019217479A (en) * | 2018-06-22 | 2019-12-26 | 株式会社石垣 | Sludge treatment method |
| JP2023127614A (en) * | 2022-03-02 | 2023-09-14 | 株式会社石垣 | Sludge treatment system |
| JP2023147394A (en) * | 2022-03-30 | 2023-10-13 | 株式会社石垣 | Sludge treatment system |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5966400A (en) * | 1982-10-08 | 1984-04-14 | Ebara Infilco Co Ltd | Floating concentration of sludge |
| JPS605300A (en) * | 1983-06-22 | 1985-01-11 | Ebara Infilco Co Ltd | Sludge dehydrating method |
-
1985
- 1985-05-22 JP JP60109651A patent/JPS61268400A/en active Pending
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5966400A (en) * | 1982-10-08 | 1984-04-14 | Ebara Infilco Co Ltd | Floating concentration of sludge |
| JPS605300A (en) * | 1983-06-22 | 1985-01-11 | Ebara Infilco Co Ltd | Sludge dehydrating method |
Cited By (18)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2010137158A (en) * | 2008-12-11 | 2010-06-24 | Kubota Kankyo Service Kk | Apparatus for measuring fiber concentration in sludge, apparatus for adjusting fiber concentration in sludge, dehydration equipment and dehydration method |
| CN101767922B (en) | 2010-01-21 | 2012-07-04 | 上海亚同环保实业股份有限公司 | Sludge dehydration treatment technology |
| JP2017100130A (en) * | 2011-04-26 | 2017-06-08 | 水ing株式会社 | Anaerobic digestion treatment method and anaerobic digestion treatment device |
| JP2013119081A (en) * | 2011-12-09 | 2013-06-17 | Kobelco Eco-Solutions Co Ltd | Treatment method and treatment apparatus for phosphorus-containing wastewater |
| US9975798B2 (en) | 2013-07-26 | 2018-05-22 | Ishigaki Company Limited | Sludge dehydration system and sludge dehydration method |
| WO2015012039A1 (en) | 2013-07-26 | 2015-01-29 | 株式会社石垣 | Recovery device and recovery method for recovering specific material from sludge, sludge dehydration system, and sludge dehydration method |
| EP3059015A1 (en) | 2013-07-26 | 2016-08-24 | Ishigaki Company Limited | Sludge dehydration system and sludge dehydration method |
| US11401188B2 (en) | 2013-07-26 | 2022-08-02 | Ishigaki Company Limited | Sludge dehydration system and sludge dehydration method |
| JP2015024371A (en) * | 2013-07-26 | 2015-02-05 | 株式会社石垣 | Extraction equipment |
| US10974982B2 (en) | 2013-07-26 | 2021-04-13 | Ishigaki Company Limited | Recovery device and recovery method for recovering specific material from sludge |
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| JP2015054287A (en) * | 2013-09-12 | 2015-03-23 | 株式会社石垣 | Sludge treatment method |
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| JP2016190188A (en) * | 2015-03-31 | 2016-11-10 | 株式会社石垣 | Sludge dewatering device and sludge dewatering method |
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| JP2019217479A (en) * | 2018-06-22 | 2019-12-26 | 株式会社石垣 | Sludge treatment method |
| JP2023127614A (en) * | 2022-03-02 | 2023-09-14 | 株式会社石垣 | Sludge treatment system |
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