EP0842125A1 - Process for treating a surplus activated sludge - Google Patents
Process for treating a surplus activated sludgeInfo
- Publication number
- EP0842125A1 EP0842125A1 EP96902522A EP96902522A EP0842125A1 EP 0842125 A1 EP0842125 A1 EP 0842125A1 EP 96902522 A EP96902522 A EP 96902522A EP 96902522 A EP96902522 A EP 96902522A EP 0842125 A1 EP0842125 A1 EP 0842125A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- activated sludge
- treating
- surplus activated
- sulfate
- pulp production
- 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.)
- Withdrawn
Links
Classifications
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/0064—Aspects concerning the production and the treatment of green and white liquors, e.g. causticizing green liquor
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
- C02F11/143—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using inorganic substances
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
- C02F11/143—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using inorganic substances
- C02F11/145—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using inorganic substances using calcium compounds
Definitions
- the present invention relates to a process foi"* treating settlings formed during the biological purification of municipal and industrial waste water and may foe used in various fields of industry, in particular in paper and pulp production.
- the main disadvantage of the known process consists an low effectiveness and high duration of a process for dehydrating the settlings by filtering, which is caused by an unfavorable structure of said settlings that firmly retain water and have a high specific filtration resist-ance.
- the known process requires the use of expensive alkaline ⁇ *eagents .-'see Y ⁇ . N. Nelepin, "Sulfate Pulp Production”, “ esnaya Promyshlennost", Moscow, l£-80, p. 531/'.
- the present invention is made in order to solve the above problems included in the prior arts, and an object of this invention is t provide a new process for treating a surplus activated sludge enabling intensification of the process fo* dehydrating the settlings by filtering, avoiding the use of expensive chemical reagents, a complete utilisation of the process products so obtained t clarified alkaline hydrolysate and an ash residue) as well as utilisation of the sulfate-pulp production waste with minimal costs.
- the present process differs from the known one in that it provides for the treatment of the pre-dehydrated surplus activated sludge with white slime obtained at the stage of cau ⁇ ticising green liquor in the process of the sulfate-pulp production, with stirring and in a volume ratio of white slime : surplus activated sludge equal to 1 : 5 - 10.
- White slime used in the present process for treating the surplus activated sludge is a sulfate-pulp production waste being a black suspension with a density of 1.25 - 1.35 Kgj/'cub. dm and having the following chemical composition, % wt. :
- Using white slime in accordance with the present process allows solution of two problems at once: on the one hand, to intensify and lower the price of the process for treating the surplus activated sludge and, on the other hand, to significantly simplify nd lower the price of the process for utilising white slime.
- a process for treating the surplus activated sludge thickened when p-resettling the precipitate, by means of white slime containing alkali residues is accompanied with practically a complete alkaline hydrolysis of the bioorganic part of the sludge (constituting no less than 83 % wt. 2 ⁇ dry residue) with the formation of salts of amino acids, amino alcohols and a number of protein derivatives.
- calcium carbonate constituting the major contents of white slime is uniformly distributed, when stirred thoroughly, among undissolved large fibres and solid particles present in the surplus activated sludge in the amount up to 17 w . on dry basis.
- the present process is carried out. m the following manne .
- the surplus activated sludge is subjected to pre- hickening in a radial or vertical pond. Most preferably, '' thickening is carried out up to the surplus activated sludge concentration of 18 - 40 g/1. Upon thickening, the surplus ' activated sludge is fed to a mixer where it is treated with white slime, while stirring. White slime is used in a volume ratio to the surplus activated sl ⁇ jdge equal to 1 : 5 - 10 which allows achievement of a maximal efficiency of post-filtering. When treating the sludge with white slime taken in the amount less than that mentioned above, a filtering rate reduces significantly. It is not to the purpose of technology to use white slime in the amounts exceeding the claimed ratio.
- stirring is carried out at a temperature of between 75 and 104 C. It is also possible to use lower temperatures, up to room temperature, but in this case a process for treating becomes more prolonged.
- the treatment is carried out to a complete dissolution of a bioorganic part of the surplus activated sludge. Then, a mixture so obtained which contains an alkaline hydrolysate, undissolved fibres and solid particles present in the surplus activated sludge, ae well as calcium carbonate uniformly distributed among the particles of sludge settlings as a result of stirring, are fed to a vacuum filter or a pressure filter and subjected to dehydration.
- a clarified alkaline hydrolysate obtained upon filtration may be used, without a subsequent treatment, in the manufacturing cycle of the sulfate-pulp production at the stage of reagent regeneration.
- a dehydrated precipitate formed on a filter surface is readily removed from the filter surface, thereupon it is subjected to heat drying in drier drums and fed to burn down in an utilisation plant furnace.
- An ash residue comprising calcium oxide is used in the manufacturing cycle of the sulfate-pulp ( production at the stage of a green liquor causticising.
- a concentration of 80 g,-l, 0.75 1 of a white slime suspension is added and thoroughly stirred for 15 minutes at 95 C.
- a mixture so obtained is fed to a vacuum filter and subjected to dehydration of the settlings.
- a filtration rate is determined to be 40 I/sq. m/rnin.
- a clarified alkaline hydrolysate is fed to be used in the manufacturing cycle of the sulfate-pulp production.
- a dehydrated precipitate formed on a filter surface is removed and subjected to heat drying at 850 C, the ⁇ v eupon it is burned down.
- An ash residue obtained is fed to the stage of a green liquor causticising.
- the present process for treating the surplus activated sludge allows intensification of the filtration process, avoiding the use of expensive chemical reagents (at. the expense of using waste of the sulfate-pulp production), a complete utilisation of products obtained when treating the sludge (an ash residue and a clarified alkaline hydrolysate) as well as utilisation of the sulfate-pulp production waste, that is white slime, with simplifica ion of the production procedures and techniques and significant reduction of material costs.
- a filtration rate in accordance with the known process is 4 i/sq. m min. Besides, reduction in a dehydration process time according to the present process results in the decrease of energy consumed to realise thereof.
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Hydrology & Water Resources (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Mechanical Engineering (AREA)
- Paper (AREA)
- Treatment Of Sludge (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
RU9595112218A RU2079454C1 (ru) | 1995-07-18 | 1995-07-18 | Способ обработки избыточного активного ила |
RU95112218 | 1995-07-18 | ||
PCT/RU1996/000032 WO1997003928A1 (en) | 1995-07-18 | 1996-02-12 | Process for treating a surplus activated sludge |
Publications (1)
Publication Number | Publication Date |
---|---|
EP0842125A1 true EP0842125A1 (en) | 1998-05-20 |
Family
ID=20170155
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP96902522A Withdrawn EP0842125A1 (en) | 1995-07-18 | 1996-02-12 | Process for treating a surplus activated sludge |
Country Status (11)
Country | Link |
---|---|
EP (1) | EP0842125A1 (no) |
JP (1) | JPH11510090A (no) |
KR (1) | KR19990028251A (no) |
CN (1) | CN1196033A (no) |
AU (1) | AU4680296A (no) |
BR (1) | BR9609736A (no) |
CA (1) | CA2224683A1 (no) |
FI (1) | FI980091A (no) |
NO (1) | NO980210L (no) |
RU (1) | RU2079454C1 (no) |
WO (1) | WO1997003928A1 (no) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109279758A (zh) * | 2018-11-21 | 2019-01-29 | 湖南骏泰新材料科技有限责任公司 | 一种绿泥高效洗涤方法 |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1295399C (zh) * | 2003-12-01 | 2007-01-17 | 中国农业科学院土壤肥料研究所 | 生活污泥-废弃塑料混聚物修复岩石坡面技术 |
CA2854292A1 (en) * | 2011-11-04 | 2013-05-10 | Valmet Ab | Method for the causticizing process for producing white liquor |
CN102491618A (zh) * | 2011-11-29 | 2012-06-13 | 曾秀仪 | 一种剩余污泥的深度脱水方法 |
CN106396308B (zh) * | 2016-10-27 | 2019-12-31 | 环境保护部华南环境科学研究所 | 一种剩余活性污泥的回收利用方法 |
CN110424179B (zh) * | 2019-08-26 | 2021-09-21 | 华南理工大学 | 一种造纸污泥焚烧后固废改性用作造纸填料的方法 |
CN112726252B (zh) * | 2020-11-30 | 2022-11-25 | 山东华泰纸业股份有限公司 | 一种造纸厂废渣的综合利用方法 |
CN112796144A (zh) * | 2020-12-28 | 2021-05-14 | 山东泗水金立得纸业有限公司 | 一种无碳复写纸产线污泥回收高岭土的方法 |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE2410394A1 (de) * | 1973-03-07 | 1974-09-12 | Andco Inc | Verfahren zum entwaessern eines waessrigen schlamms dispergierten, fein zerkleinerten feststoffes |
US4030968A (en) * | 1975-12-22 | 1977-06-21 | Consolidated-Bathurst Limited | Disposal of paper pulp mill sludge |
NL7707081A (nl) * | 1977-06-27 | 1978-12-29 | Stamicarbon | Werkwijze voor het biologisch zuiveren van afvalwater. |
SU1038287A1 (ru) * | 1979-11-20 | 1983-08-30 | Всесоюзное научно-производственное объединение целлюлозно-бумажной промышленности | Способ обработки избыточного активного ила |
DE3043518C2 (de) * | 1979-11-20 | 1985-08-01 | Amurskij celljulozno-kartonnyj kombinat, Amursk | Verfahren zur Rückgewinnung von Abwässerniederschlägen bzw. -rückständen |
-
1995
- 1995-07-18 RU RU9595112218A patent/RU2079454C1/ru active
-
1996
- 1996-02-12 AU AU46802/96A patent/AU4680296A/en not_active Abandoned
- 1996-02-12 JP JP9506587A patent/JPH11510090A/ja active Pending
- 1996-02-12 CN CN96196796A patent/CN1196033A/zh active Pending
- 1996-02-12 WO PCT/RU1996/000032 patent/WO1997003928A1/en active IP Right Grant
- 1996-02-12 CA CA002224683A patent/CA2224683A1/en not_active Abandoned
- 1996-02-12 EP EP96902522A patent/EP0842125A1/en not_active Withdrawn
- 1996-02-12 BR BR9609736-1A patent/BR9609736A/pt not_active Application Discontinuation
- 1996-02-12 KR KR1019970709562A patent/KR19990028251A/ko active IP Right Grant
-
1998
- 1998-01-16 FI FI980091A patent/FI980091A/fi unknown
- 1998-01-16 NO NO980210A patent/NO980210L/no unknown
Non-Patent Citations (1)
Title |
---|
See references of WO9703928A1 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109279758A (zh) * | 2018-11-21 | 2019-01-29 | 湖南骏泰新材料科技有限责任公司 | 一种绿泥高效洗涤方法 |
Also Published As
Publication number | Publication date |
---|---|
CN1196033A (zh) | 1998-10-14 |
RU2079454C1 (ru) | 1997-05-20 |
FI980091A0 (fi) | 1998-01-16 |
FI980091A (fi) | 1998-01-16 |
KR19990028251A (ko) | 1999-04-15 |
WO1997003928A1 (en) | 1997-02-06 |
BR9609736A (pt) | 1999-12-21 |
NO980210D0 (no) | 1998-01-16 |
AU4680296A (en) | 1997-02-18 |
NO980210L (no) | 1998-01-16 |
CA2224683A1 (en) | 1997-02-06 |
JPH11510090A (ja) | 1999-09-07 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106746124A (zh) | 垃圾飞灰水洗预处理及水泥窑协同资源化处置系统 | |
US2613181A (en) | Treatment of oily waste water | |
EP0842125A1 (en) | Process for treating a surplus activated sludge | |
WO1988006203A1 (en) | Method for green liquor cleaning in sulphate pulp mills | |
CN107055886B (zh) | 一种深度递级分盐工艺 | |
JPS58131200A (ja) | 汚泥の処理方法 | |
JPS5949078B2 (ja) | 汚泥処理方法 | |
US4038181A (en) | Process for dewatering sewage sludge | |
CN108947085A (zh) | 高盐废水雾化回收处理方法 | |
US2734037A (en) | Method of introducing sulfite waste | |
US3163598A (en) | Method for disposal of industrial waste water | |
RU2071940C1 (ru) | Способ переработки дистиллерной суспензии аммиачно-содового производства | |
JP2009018271A (ja) | リンの除去を行う廃水処理方法及び装置 | |
JPH0122840B2 (no) | ||
DK158141B (da) | Fremgangsmaade til fremstilling af en anionbytter samt anvendelse heraf | |
SU1038287A1 (ru) | Способ обработки избыточного активного ила | |
SU1283227A1 (ru) | Способ очистки сточных вод масложировой промышленности | |
JPH021560B2 (no) | ||
RU2167969C1 (ru) | Способ промывки каустизационного шлама крепкого белого щелока | |
US3349921A (en) | Process for converting sulfate pump waste residues into high utility material and means of applying same | |
SU791650A1 (ru) | Способ обработки осадка сточных вод | |
SU1010170A1 (ru) | Способ обработки отработанных химикатов натронного производства полуцеллюлозы | |
SU1260364A1 (ru) | Способ обезвоживани птичьего помета | |
SU859310A1 (ru) | Способ обработки продувочных вод парогенераторов | |
SU1662952A1 (ru) | Способ обработки осадков сточных вод |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PUAI | Public reference made under article 153(3) epc to a published international application that has entered the european phase |
Free format text: ORIGINAL CODE: 0009012 |
|
17P | Request for examination filed |
Effective date: 19980216 |
|
AK | Designated contracting states |
Kind code of ref document: A1 Designated state(s): AT BE DE ES FR PT SE |
|
RIN1 | Information on inventor provided before grant (corrected) |
Inventor name: GRUDININ, VLADIMIROVICH ALEXANDR Inventor name: GRUDININ, VLADIMIR PAVLOVICH |
|
STAA | Information on the status of an ep patent application or granted ep patent |
Free format text: STATUS: THE APPLICATION IS DEEMED TO BE WITHDRAWN |
|
18D | Application deemed to be withdrawn |
Effective date: 19990831 |