EP0842125A1 - Process for treating a surplus activated sludge - Google Patents

Process for treating a surplus activated sludge

Info

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Withdrawn
Application number
EP96902522A
Other languages
German (de)
English (en)
French (fr)
Inventor
Vladimir Pavlovich Grudinin
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.)
Anisimov Alexandr Pavlovich
Original Assignee
Anisimov Alexandr Pavlovich
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 Anisimov Alexandr Pavlovich filed Critical Anisimov Alexandr Pavlovich
Publication of EP0842125A1 publication Critical patent/EP0842125A1/en
Withdrawn legal-status Critical Current

Links

Classifications

    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C11/00Regeneration of pulp liquors or effluent waste waters
    • D21C11/0064Aspects concerning the production and the treatment of green and white liquors, e.g. causticizing green liquor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • C02F11/143Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using inorganic substances
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • C02F11/143Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using inorganic substances
    • C02F11/145Treatment 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)
EP96902522A 1995-07-18 1996-02-12 Process for treating a surplus activated sludge Withdrawn EP0842125A1 (en)

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)

* Cited by examiner, † Cited by third party
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)

* Cited by examiner, † Cited by third party
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)

* Cited by examiner, † Cited by third party
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

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO9703928A1 *

Cited By (1)

* Cited by examiner, † Cited by third party
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

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Legal Events

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PUAI Public reference made under article 153(3) epc to a published international application that has entered the european phase

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Effective date: 19980216

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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