JPS5881499A - Treatment of sludge - Google Patents
Treatment of sludgeInfo
- Publication number
- JPS5881499A JPS5881499A JP56180556A JP18055681A JPS5881499A JP S5881499 A JPS5881499 A JP S5881499A JP 56180556 A JP56180556 A JP 56180556A JP 18055681 A JP18055681 A JP 18055681A JP S5881499 A JPS5881499 A JP S5881499A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- incineration ash
- dehydration
- ash
- coal
- 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】
この発明は、汚泥からの脱水を促進する処理方法に関す
るものであり、この明細書全体において、汚泥とは、下
水、尿尿、家畜排水、産業排水の汚水処理によって発生
した汚泥、糞尿及びこれら濃縮物の総称として用いる。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a treatment method for promoting dewatering from sludge, and throughout this specification, sludge refers to sludge generated through the treatment of sewage, urine, livestock wastewater, and industrial wastewater. It is used as a general term for sludge, excrement, and their concentrates.
省エネルギ化が図られている昨今、汚泥の有効利用を図
るだめ、汚泥を自然脱水させて、肥料化、或いは燃料化
することが行なわれている。しかし、自然脱水させるに
は2〜3ケ月と長期間かかり、更にその脱水期間中悪臭
を発生するという問題があり、肥料化、燃料化するには
住宅街から遠く離れた場所に広大な敷地が必要であった
。BACKGROUND ART Nowadays, in an effort to save energy, in order to make effective use of sludge, sludge is naturally dehydrated and turned into fertilizer or fuel. However, natural dehydration takes a long time, 2 to 3 months, and there is a problem in that it produces a bad odor during the dehydration period, and it requires a large plot of land far from residential areas to turn it into fertilizer or fuel. It was necessary.
また、汚泥は焼却処理もされるが、その焼却灰の喰が増
加し、その処理が問題となっている。また火力発電所に
おける燃料の石炭への切換により、石炭灰の増加も問題
となっている。Furthermore, sludge is also treated by incineration, but the amount of incinerated ash increases and its disposal becomes a problem. Furthermore, due to the switch to coal as fuel at thermal power plants, an increase in coal ash has also become a problem.
この発明は、これら両問題を一挙に解決することを目的
としてなされたもので、処理に困っている上記の焼却灰
(石炭灰を含む)を混入攪拌し、汚泥からの脱水を促進
し、肥料化、燃料化をはやめ、併せて脱臭も行なうもの
である。This invention was made with the aim of solving both of these problems at once.The above-mentioned incineration ash (including coal ash), which is difficult to dispose of, is mixed in and stirred to promote dewatering from the sludge, and to make fertilizer. This process not only reduces the amount of oxidation and fuel used, but also deodorizes it.
この発明が脱水、蜆臭効果を有することは、次の2つの
実験より明らかである。It is clear from the following two experiments that this invention has effects on dehydration and odor.
第1の実験は、合板工場の廃水1oOmlに製紙工場の
汚泥の焼却灰xgを混入攪拌し、次亜塩素酸ナト・・リ
ウムを添加攪拌し、塩化第二鉄でPHを酸にし、苛性ソ
ーダで中性に戻し、最後に高分子でフロックを作り、完
全に沈降させたものと、上記の廃水そのものとをそれぞ
れ18・5.NO,3の濾紙で濾過するのに有する時間
を測定したものである。なお、上記の焼却灰は、Siを
12.62 % 、AIをq、53 % 、 Feを0
.36% 、Caを1.04%含み、X線回折等からA
N2 S140よ。(OH)2が存在していると考えら
れるものである。その結果を下表に示す。The first experiment was to mix xg of incinerated ash from paper mill sludge into 1oOml of wastewater from a plywood factory, stir it, add sodium hypochlorite and stir, acidify the pH with ferric chloride, and add caustic soda to the mixture. The mixture was returned to neutrality, and finally, flocs were made with a polymer and completely settled, and the wastewater itself was mixed at 18.5. The time required for filtration with NO.3 filter paper was measured. The above incineration ash contains 12.62% Si, q, 53% AI, and 0 Fe.
.. 36%, contains 1.04% Ca, and is A from X-ray diffraction etc.
N2 S140. It is thought that (OH)2 is present. The results are shown in the table below.
第2の実験は、含水率90%の豚の糞尿100 fに対
して、上記の焼却灰lOg、2of 、30pそれぞれ
混入し、5分間攪拌したものと、豚の糞尿1009その
ままのものとを直径18・5crnN0.3の濾紙上に
置き、日陰に放ill L、毎日午前9時に含水量及び
臭いを測定したものである。In the second experiment, 100 f of pig manure with a moisture content of 90% was mixed with 10 g, 2 of, and 30 p of the above-mentioned incinerated ash and stirred for 5 minutes. The sample was placed on a 18.5crnN0.3 filter paper, left in the shade, and the moisture content and odor were measured at 9:00 a.m. every day.
これら両実験結果からも判るように、処分に困まる製紙
汚泥等の焼却灰を糞尿に混入攪拌することによシ、糞尿
からの脱水を促進することができ、肥料化あるいは燃料
化を早めることができ、しかも早急に脱臭できるので悪
臭による二次公害の発生もなく、住宅街に近い場所でこ
のような処理を行なっても問題が生じない。従って、焼
却灰の処理と同時に糞尿の処理もでき、有効である。ま
た脱水が早急に行なわれるので、自然脱水した場合に大
量に発生するウジ虫もほとんど発生せず、衛生的である
。As can be seen from the results of both of these experiments, by mixing incineration ash such as paper sludge, which is difficult to dispose of, with manure and stirring it, it is possible to accelerate the dehydration of manure and accelerate its conversion into fertilizer or fuel. Moreover, since it can quickly deodorize, there is no secondary pollution caused by bad odors, and there are no problems even if this type of treatment is performed in a place near a residential area. Therefore, it is possible to treat excrement and urine at the same time as incineration ash, which is effective. Furthermore, since dehydration is carried out quickly, there are almost no maggots, which occur in large quantities when natural dehydration occurs, and it is hygienic.
この発明の実施例としては、上記の汚泥に対し上記の焼
却灰を混入攪拌し、真空脱水4機等の脱水機にかけるも
のが考えられる。この場″合、第1の実験結果より脱水
機の目詰シかほとんどないことが容易、に理解される。As an embodiment of the present invention, it is conceivable that the above-mentioned sludge is mixed with the above-mentioned incineration ash, stirred, and then subjected to a dehydrator such as a vacuum dehydrator 4. In this case, it is easily understood from the first experimental results that there is almost no clogging of the dehydrator.
なお、上記の実験、には製紙汚泥の焼却灰を用いたが、
他に石炭の焼却灰、例えば砲をo、3o % 、Naを
0.99%、Caを2.03%、Fe1o、s7%、5
102を12.63係、Alを゛2.80チ含み、強・
熱誠量+水分46.2チで、他にX線回析から5102
、CaCO3の存在が考えられるものや、都市下水汚泥
例えばMgを0・89%、 Naを1.46 % %C
aを24.67 % 、Feを3.32 % 、5in
2を21.9 i%、A6を6.25%含み、強熱減量
+水分が12・0%でX線回析から5in2、CaCO
3が存在すると考えられるものや、都市ゴミの焼却灰、
家畜の糞尿等の焼却灰も同様に使用できることが判って
いる。また、第2の実験には豚の糞尿を用いたが、これ
ら以外吟も鶏糞、牛糞、人糞あるいはそれらの濃縮物に
も適用できる。Incidentally, in the above experiment, incineration ash of paper manufacturing sludge was used.
In addition, coal incineration ash, such as gun o, 3o%, Na 0.99%, Ca 2.03%, Fe1o, s7%, 5
Contains 12.63 parts of 102, 2.80 parts of Al, strong
The amount of sincerity + moisture is 46.2%, and from X-ray diffraction it is 5102%.
, those where the presence of CaCO3 is considered, and urban sewage sludge such as Mg 0.89%, Na 1.46%%C
24.67% a, 3.32% Fe, 5in
CaCO
3 is thought to exist, incineration ash of municipal garbage,
It has been found that incinerated ash, such as livestock manure, can be used in a similar manner. Further, although pig manure was used in the second experiment, other materials such as chicken manure, cow manure, human manure, or concentrates thereof can also be applied.
特許出願人 武 1) 睦Patent applicant Takeshi 1) Mutsumi
Claims (1)
汚泥の処理方法。(11. A sludge treatment method characterized by mixing incineration ash with sludge and stirring.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56180556A JPS5881499A (en) | 1981-11-10 | 1981-11-10 | Treatment of sludge |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56180556A JPS5881499A (en) | 1981-11-10 | 1981-11-10 | Treatment of sludge |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS5881499A true JPS5881499A (en) | 1983-05-16 |
Family
ID=16085337
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP56180556A Pending JPS5881499A (en) | 1981-11-10 | 1981-11-10 | Treatment of sludge |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5881499A (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS59142900A (en) * | 1983-02-04 | 1984-08-16 | Mitsubishi Kakoki Kaisha Ltd | Method for utilizing incineration ash of screening as dehydrating auxiliary for sludge |
JP2011050910A (en) * | 2009-09-03 | 2011-03-17 | Sumitomo Heavy Industries Environment Co Ltd | Method and apparatus for biological wastewater treatment |
CN102206031A (en) * | 2011-04-26 | 2011-10-05 | 周悦先 | Cleaning agent for urban sewage sludge and sludge treatment method |
CN102992464A (en) * | 2012-12-06 | 2013-03-27 | 首钢总公司 | Disposal method for high-salinity wastewater and waste incineration fly ash |
CN104628235A (en) * | 2015-02-28 | 2015-05-20 | 西安市利生污泥处理有限公司 | Sludge deodorant as well as preparation method and application thereof |
-
1981
- 1981-11-10 JP JP56180556A patent/JPS5881499A/en active Pending
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS59142900A (en) * | 1983-02-04 | 1984-08-16 | Mitsubishi Kakoki Kaisha Ltd | Method for utilizing incineration ash of screening as dehydrating auxiliary for sludge |
JP2011050910A (en) * | 2009-09-03 | 2011-03-17 | Sumitomo Heavy Industries Environment Co Ltd | Method and apparatus for biological wastewater treatment |
CN102206031A (en) * | 2011-04-26 | 2011-10-05 | 周悦先 | Cleaning agent for urban sewage sludge and sludge treatment method |
CN102992464A (en) * | 2012-12-06 | 2013-03-27 | 首钢总公司 | Disposal method for high-salinity wastewater and waste incineration fly ash |
CN104628235A (en) * | 2015-02-28 | 2015-05-20 | 西安市利生污泥处理有限公司 | Sludge deodorant as well as preparation method and application thereof |
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