WO2006074618A1 - Sludge from sewage treatment plants - Google Patents

Sludge from sewage treatment plants Download PDF

Info

Publication number
WO2006074618A1
WO2006074618A1 PCT/CZ2005/000098 CZ2005000098W WO2006074618A1 WO 2006074618 A1 WO2006074618 A1 WO 2006074618A1 CZ 2005000098 W CZ2005000098 W CZ 2005000098W WO 2006074618 A1 WO2006074618 A1 WO 2006074618A1
Authority
WO
WIPO (PCT)
Prior art keywords
sludge
sewage treatment
treatment plants
biologically
distinguished
Prior art date
Application number
PCT/CZ2005/000098
Other languages
French (fr)
Other versions
WO2006074618A8 (en
Inventor
Lubos Hajek
Original Assignee
Lubos Hajek
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 Lubos Hajek filed Critical Lubos Hajek
Priority to EP05819248A priority Critical patent/EP1856000A1/en
Publication of WO2006074618A1 publication Critical patent/WO2006074618A1/en
Publication of WO2006074618A8 publication Critical patent/WO2006074618A8/en

Links

Classifications

    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
    • C05D3/00—Calcareous fertilisers
    • 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
    • C02F11/147—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using organic substances
    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F3/00—Fertilisers from human or animal excrements, e.g. manure
    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F7/00—Fertilisers from waste water, sewage sludge, sea slime, ooze or similar masses
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00—Use of specific compounds during water treatment
    • C02F2305/06—Nutrients for stimulating the growth of microorganisms
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00—Technologies relating to chemical industry
    • Y02P20/141—Feedstock
    • Y02P20/145—Feedstock the feedstock being materials of biological origin

Definitions

  • the invention relates to sludge from sewage treatment plants.
  • Sludge from sewage treatment plants is often treated with the purpose of obtaining material for soil recultivation and for use in agriculture and forestry. It is for this purpose that the sludge is being enriched, depending on its determined usage, for example by ash from heating power plants, products accrued from desulphurization of heating power plants, and organic material of animal or plant origin.
  • the resulted material is then used for filling an area that has been depreciated by previous usage.
  • a disadvantage of using such materials is the release of various forms of nitrogen, nutrients, heavy metals and their chemical forms, which cause unwanted contamination of soil and consequently also water.
  • Another disadvantage of stowing such a material is also a possible occurrence of gas production causing a green house effect, which is caused by the imperfect degradation of organic mass, for example of methane and carbon dioxide.
  • the objective of this invention is therefore to create such a substance for recultivation that is physically as well as biologically stable and significantly decreases the production of environment contaminants, while it is also suitable for usage in the areas of agriculture and forestry.
  • the essence of the sludge from sewage treatment plants according to this invention lies in the fact that it contains an addition of a biologically enzymatic compound with bound microorganisms.
  • the basic material can possibly contain an addition of mineral or nutritive material on a base of crushed mineral or organic mass.
  • the weight concentration of the biologically enzymatic compound with bound microorganisms is in the range of 0.02 through 5 percent when measured as of the laboratory sludge dry residue of the basic material.
  • the material advantageously contains ash from burning coal and solid reaction products on a calcium base from flue gas desulphurization.
  • the material When used in the areas of agriculture, forestry, and horticulture, the material contains waste of plant tissues, animal excrement, and manure including polluted straw and farm organic products, possibly also forestry waste.
  • a biologically enzymatic compound with bound microorganisms is added to the sludge from sewage treatment plants.
  • the weight concentration of the biologically enzymatic compound with bound microorganisms in the sludge is in the range of 0.1 through 1 percent.
  • the biologically enzymatic compound is represented especially by saprophyte microbiological strains that decompose organic mass under aerobic or anaerobic conditions; these strains can be possibly bound to a suitable mineral protective medium.
  • the biologically enzymatic compound with bound microorganisms is, before added to the sludge, mixed with yet another addition, for example with mineral or nutritive material on a base of crushed mineral or organic mass
  • the final content of the biologically enzymatic compound with bound microorganisms in the sludge is proportionately higher by the added addition.
  • the content of this bio compound in the sludge moves within the optimal effective range of 0.1 through 5 percent.
  • Sludge modified in this way is advantageously used not only for soil recultivation, but also as a fertilizer especially in agriculture, forestry, and horticulture.
  • the sludge When using the sludge for soil recultivation, it contains, as yet another addition, ash from burning coal and solid reaction products on a calcium base from flue gas desulphurization.
  • another addition of the sludge is the waste of plant tissues, animal excrement, and manure including polluted straw and farm organic products, possibly also forestry waste.

Abstract

The invention relates to sludge from sewage treatment plants that contains an addition of biologically enzymatic compound with bound microorganisms. Its other addition is mineral or nutritive material on a base of crushed mineral or organic mass. The weight concentration of the biologically enzymatic compound with bound microorganisms is in the range of 0.02 through 5 percent of the laboratory sludge dry residue. For recultivation purposes, the sludge further contains ash from burning coal and solid reaction products on a calcium base from flue gas desulphurization. For the purposes of valorizing soil in the area of agriculture, forestry, and horticulture, the sludge contains the waste of plant tissues, animal excrement, and manure including polluted straw and farm organic products, possibly also forestry waste.

Description

Sludge from sewage treatment plants
The invention relates to sludge from sewage treatment plants.
Sludge from sewage treatment plants is often treated with the purpose of obtaining material for soil recultivation and for use in agriculture and forestry. It is for this purpose that the sludge is being enriched, depending on its determined usage, for example by ash from heating power plants, products accrued from desulphurization of heating power plants, and organic material of animal or plant origin.
The resulted material is then used for filling an area that has been depreciated by previous usage. A disadvantage of using such materials is the release of various forms of nitrogen, nutrients, heavy metals and their chemical forms, which cause unwanted contamination of soil and consequently also water.
Another disadvantage of stowing such a material is also a possible occurrence of gas production causing a green house effect, which is caused by the imperfect degradation of organic mass, for example of methane and carbon dioxide.
The objective of this invention is therefore to create such a substance for recultivation that is physically as well as biologically stable and significantly decreases the production of environment contaminants, while it is also suitable for usage in the areas of agriculture and forestry.
Summary of the invention
The essence of the sludge from sewage treatment plants according to this invention lies in the fact that it contains an addition of a biologically enzymatic compound with bound microorganisms. The basic material can possibly contain an addition of mineral or nutritive material on a base of crushed mineral or organic mass.
The weight concentration of the biologically enzymatic compound with bound microorganisms is in the range of 0.02 through 5 percent when measured as of the laboratory sludge dry residue of the basic material.
The material advantageously contains ash from burning coal and solid reaction products on a calcium base from flue gas desulphurization.
When used in the areas of agriculture, forestry, and horticulture, the material contains waste of plant tissues, animal excrement, and manure including polluted straw and farm organic products, possibly also forestry waste. Application Example of Invention
A biologically enzymatic compound with bound microorganisms is added to the sludge from sewage treatment plants. When using the sludge itself, the weight concentration of the biologically enzymatic compound with bound microorganisms in the sludge is in the range of 0.1 through 1 percent.
The biologically enzymatic compound is represented especially by saprophyte microbiological strains that decompose organic mass under aerobic or anaerobic conditions; these strains can be possibly bound to a suitable mineral protective medium.
In the case that the biologically enzymatic compound with bound microorganisms is, before added to the sludge, mixed with yet another addition, for example with mineral or nutritive material on a base of crushed mineral or organic mass, the final content of the biologically enzymatic compound with bound microorganisms in the sludge is proportionately higher by the added addition. The content of this bio compound in the sludge moves within the optimal effective range of 0.1 through 5 percent.
Sludge modified in this way is advantageously used not only for soil recultivation, but also as a fertilizer especially in agriculture, forestry, and horticulture.
When using the sludge for soil recultivation, it contains, as yet another addition, ash from burning coal and solid reaction products on a calcium base from flue gas desulphurization. hi the case of using the sludge as a fertilizer in agriculture, forestry, and horticulture, another addition of the sludge is the waste of plant tissues, animal excrement, and manure including polluted straw and farm organic products, possibly also forestry waste.

Claims

1.
Sludge from sewage treatment plants distinguished by the fact that it contains an addition of biologically enzymatic compound with bound microorganisms.
2.
Sludge from sewage treatment plants in compliance with requirement 1 distinguished by the fact that it contains mineral or nutritive material on a base of crushed mineral or organic mass.
3.
Sludge from sewage treatment plants in compliance with one of the above mentioned requirements distinguished by the fact that the weight concentration of the biologically enzymatic compound with bound microorganisms is in the range of 0.02 through 5 percent of the laboratory sludge dry residue.
4.
Sludge from sewage treatment plants in compliance with requirements 1 through 3 distinguished by the fact that it contains ash from burning coal and solid reaction products on a calcium base from flue gas desulphurization.
5.
Sludge from sewage treatment plants in compliance with requirements 1 through 3 distinguished by the fact that it contains waste of plant tissues, animal excrement, and manure including polluted straw and farm organic products, possibly also forestry waste.
PCT/CZ2005/000098 2005-01-07 2005-12-21 Sludge from sewage treatment plants WO2006074618A1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
EP05819248A EP1856000A1 (en) 2005-01-07 2005-12-21 Sludge from sewage treatment plants

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CZ200511A CZ308871B6 (en) 2005-01-07 2005-01-07 Sludge from sewage treatment plants
CZPV2005-11 2005-01-07

Publications (2)

Publication Number Publication Date
WO2006074618A1 true WO2006074618A1 (en) 2006-07-20
WO2006074618A8 WO2006074618A8 (en) 2009-02-05

Family

ID=36072190

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/CZ2005/000098 WO2006074618A1 (en) 2005-01-07 2005-12-21 Sludge from sewage treatment plants

Country Status (3)

Country Link
EP (1) EP1856000A1 (en)
CZ (1) CZ308871B6 (en)
WO (1) WO2006074618A1 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103864482A (en) * 2014-02-25 2014-06-18 湖北万丰化工有限公司 Biological organic fertilizer and preparation process thereof
NL2014902A (en) * 2015-05-13 2016-05-24 The Triple E Trust Holding B V Soil improver comprising sludge containing mycorrhiza, and method for manufacturing the soil improver.
CN108083864A (en) * 2018-01-17 2018-05-29 江苏华美达生物能源有限公司 A kind of livestock and poultry fecal pollution and processing factory's debirs and stalk cooperative processing method
CN108794179A (en) * 2018-07-07 2018-11-13 安徽爱能洁生物科技有限公司 A kind of bio-feritlizer of prevention soil hardening
CN113578919A (en) * 2021-07-19 2021-11-02 上海大学 Method for improving dehydration performance of kitchen waste anaerobic digestion biogas residues

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0557078A1 (en) * 1992-02-20 1993-08-25 N-Viro Energy Systems Ltd. Process to stabilize wastewater sludge
EP0630664A1 (en) * 1991-12-24 1994-12-28 Teruo Higa Microbiological method for disposing of organic waste materials
CZ191693A3 (en) * 1993-09-15 1995-04-12 Hylmar Bohumil Method of treating liquid manure and other organic waste
US5602065A (en) * 1993-06-25 1997-02-11 Higa; Teruo Process for preparing functional ceramics
JPH0959081A (en) * 1995-08-21 1997-03-04 Shoichi Yamamura Treatment of sludge
JP2003055081A (en) * 2001-08-10 2003-02-26 Futaba Green Doboku Kk Sludge fermented fertilizer
JP2004025044A (en) * 2002-06-26 2004-01-29 Hiroyuki Tanaka Method of making feed, fertilizer and soil conditioner from organismic waste by using cellular wall crushing pr0cess

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0630664A1 (en) * 1991-12-24 1994-12-28 Teruo Higa Microbiological method for disposing of organic waste materials
EP0557078A1 (en) * 1992-02-20 1993-08-25 N-Viro Energy Systems Ltd. Process to stabilize wastewater sludge
US5602065A (en) * 1993-06-25 1997-02-11 Higa; Teruo Process for preparing functional ceramics
CZ191693A3 (en) * 1993-09-15 1995-04-12 Hylmar Bohumil Method of treating liquid manure and other organic waste
CZ283175B6 (en) * 1993-09-15 1998-01-14 Bohumil Ing. Hylmar Liquefying and treating process of organic waste, particularly liquid manure of domestic animals by biological way
JPH0959081A (en) * 1995-08-21 1997-03-04 Shoichi Yamamura Treatment of sludge
JP2003055081A (en) * 2001-08-10 2003-02-26 Futaba Green Doboku Kk Sludge fermented fertilizer
JP2004025044A (en) * 2002-06-26 2004-01-29 Hiroyuki Tanaka Method of making feed, fertilizer and soil conditioner from organismic waste by using cellular wall crushing pr0cess

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
DATABASE EPODOC EUROPEAN PATENT OFFICE, THE HAGUE, NL; "Method of treating liquid manure and other organic waste", XP002374811 *
PATENT ABSTRACTS OF JAPAN vol. 1997, no. 07 31 July 1997 (1997-07-31) *
PATENT ABSTRACTS OF JAPAN vol. 2003, no. 06 3 June 2003 (2003-06-03) *
PATENT ABSTRACTS OF JAPAN vol. 2003, no. 12 5 December 2003 (2003-12-05) *

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103864482A (en) * 2014-02-25 2014-06-18 湖北万丰化工有限公司 Biological organic fertilizer and preparation process thereof
NL2014902A (en) * 2015-05-13 2016-05-24 The Triple E Trust Holding B V Soil improver comprising sludge containing mycorrhiza, and method for manufacturing the soil improver.
CN108083864A (en) * 2018-01-17 2018-05-29 江苏华美达生物能源有限公司 A kind of livestock and poultry fecal pollution and processing factory's debirs and stalk cooperative processing method
CN108794179A (en) * 2018-07-07 2018-11-13 安徽爱能洁生物科技有限公司 A kind of bio-feritlizer of prevention soil hardening
CN113578919A (en) * 2021-07-19 2021-11-02 上海大学 Method for improving dehydration performance of kitchen waste anaerobic digestion biogas residues
CN113578919B (en) * 2021-07-19 2022-09-09 上海大学 Method for improving dehydration performance of kitchen waste anaerobic digestion biogas residues

Also Published As

Publication number Publication date
WO2006074618A8 (en) 2009-02-05
CZ308871B6 (en) 2021-07-28
CZ200511A3 (en) 2006-09-13
EP1856000A1 (en) 2007-11-21

Similar Documents

Publication Publication Date Title
Waqas et al. Optimizing the process of food waste compost and valorizing its applications: A case study of Saudi Arabia
Banegas et al. Composting anaerobic and aerobic sewage sludges using two proportions of sawdust
Insam et al. Manure-based biogas fermentation residues–friend or foe of soil fertility?
Scaglia et al. Sanitation ability of anaerobic digestion performed at different temperature on sewage sludge
Sinha et al. Vermistabilization of sewage sludge (biosolids) by earthworms: converting a potential biohazard destined for landfill disposal into a pathogen-free, nutritive and safe biofertilizer for farms
Zorpas et al. Combination of Fenton oxidation and composting for the treatment of the olive solid residue and the olive mile wastewater from the olive oil industry in Cyprus
Anwar et al. Characterization and recycling of organic waste after co-composting-A review
Muscolo et al. Three different methods for turning olive pomace in resource: Benefits of the end products for agricultural purpose
Saludes et al. Characterization of dairy cattle manure/wallboard paper compost mixture
Nozhevnikova et al. Composition of a microbial community at different stages of composting and the prospects for compost production from municipal organic waste
KR20130123276A (en) Method for treating wastewater and composting of organic wastes
Rorat et al. Earthworms converting domestic and food industry wastes into biofertilizer
Kuryntseva et al. Changes in the ecological properties of organic wastes during their biological treatment
López-López et al. Impact of fertilisation practices on soil respiration, as measured by the metabolic index of short-term nitrogen input behaviour
Majumdar et al. Emission of methane and carbon dioxide and earthworm survival during composting of pharmaceutical sludge and spent mycelia
WO2006074618A1 (en) Sludge from sewage treatment plants
Gupta et al. Vermitechnology for organic waste recycling
RU2584031C1 (en) Method of processing oil sludge and cleaning oil contaminated soil
Ahmad et al. Potential of compost for sustainable crop production and soil health
Antonious Recycling organic waste for enhancing soil urease and invertase activity
Bazrafshan et al. Evaluation of microbiological and chemical parameters during wastewater Sludge and Sawdust Co-composting
Udume et al. Composting: A low-cost biotechnological approach to ameliorating macrophyte nuisance in fresh waters
Dindar et al. Effects of canned food industry sludge amendment on enzyme activities in soil with earthworms.
CZ202275A3 (en) Sludge from sewage treatment plants
Pastorelli et al. Effects of Anaerobic Digestates and Biochar Amendments on Soil Health, Greenhouse Gas Emissions, and Microbial Communities: A Mesocosm Study

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application
NENP Non-entry into the national phase

Ref country code: DE

WWE Wipo information: entry into national phase

Ref document number: 2005819248

Country of ref document: EP

WWP Wipo information: published in national office

Ref document number: 2005819248

Country of ref document: EP