WO2013068468A1 - Substances and methods for treating sludge or ash, in particular sewage sludge - Google Patents

Substances and methods for treating sludge or ash, in particular sewage sludge Download PDF

Info

Publication number
WO2013068468A1
WO2013068468A1 PCT/EP2012/072147 EP2012072147W WO2013068468A1 WO 2013068468 A1 WO2013068468 A1 WO 2013068468A1 EP 2012072147 W EP2012072147 W EP 2012072147W WO 2013068468 A1 WO2013068468 A1 WO 2013068468A1
Authority
WO
WIPO (PCT)
Prior art keywords
substance
sludge
ash
fabric
units
Prior art date
Application number
PCT/EP2012/072147
Other languages
German (de)
French (fr)
Inventor
Zoltán BOLDIZSÁR
Original Assignee
Boldizsar Zoltan
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 Boldizsar Zoltan filed Critical Boldizsar Zoltan
Publication of WO2013068468A1 publication Critical patent/WO2013068468A1/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/20Bacteria; Culture media therefor
    • 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
    • C02F11/122Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
    • 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
    • C02F11/147Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using organic 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
    • C02F11/148Combined use of inorganic and organic substances, being added in the same treatment step
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/10Addition or removal of substances other than water or air to or from the material during the treatment
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/20Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/40Treatment of liquids or slurries
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F7/00Fertilisers from waste water, sewage sludge, sea slime, ooze or similar masses
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01RELECTRICALLY-CONDUCTIVE CONNECTIONS; STRUCTURAL ASSOCIATIONS OF A PLURALITY OF MUTUALLY-INSULATED ELECTRICAL CONNECTING ELEMENTS; COUPLING DEVICES; CURRENT COLLECTORS
    • H01R4/00Electrically-conductive connections between two or more conductive members in direct contact, i.e. touching one another; Means for effecting or maintaining such contact; Electrically-conductive connections having two or more spaced connecting locations for conductors and using contact members penetrating insulation
    • H01R4/58Electrically-conductive connections between two or more conductive members in direct contact, i.e. touching one another; Means for effecting or maintaining such contact; Electrically-conductive connections having two or more spaced connecting locations for conductors and using contact members penetrating insulation characterised by the form or material of the contacting members
    • H01R4/62Connections between conductors of different materials; Connections between or with aluminium or steel-core aluminium conductors
    • H01R4/625Soldered or welded connections
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/145Feedstock the feedstock being materials of biological origin
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Definitions

  • the invention relates to substances and processes for the treatment of sludges or ashes or mixtures thereof, in particular of sewage sludge. More particularly, the invention relates to substances and processes which enable the use of the sludges and / or ashes as fertilizer or building material.
  • Sewage disposal involves the production of large quantities of sewage sludge, which to a significant extent consists of solids.
  • To reduce the volume of sewage sludge is treated anaerobically in digestion towers, whereby the amount of solids can be reduced.
  • the resulting stabilized sewage sludge is due to the high phosphate and nutrient content in principle as a fertilizer, with a use of this heavy metals can also occur contrary to this use. Only a small part of the sewage sludge is used for the fertilization. The larger part has to be burned.
  • the object of the invention is to provide substances and methods to improve the utilization of sludges and / or ashes as fertilizer and to enable use as a building material.
  • the first substance includes effective microorganisms (EM), water and disinfecting and / or odor neutralizing chemicals.
  • EM effective microorganisms
  • the latter are preferably saponins and glycols, in particular triethylene glycol.
  • sugarcane molasses or other nutrient for bacteria may also be added to properly control the life of the effective microorganisms.
  • an increase in the number of organisms EM breeding
  • the saponin or other chemicals can be added wholly or partially afterwards.
  • saponins examples include aglycones, in particular steroid saponins, steroid alkaloid saponins and / or triterpene saponins.
  • the saponins may also be of natural origin, such as from soapnut.
  • triethylene glycol are cyclodextrins.
  • Effective microorganisms are usually a mixture of various naturally occurring microorganisms. The most common is a large proportion of lactic acid bacteria, yeasts, especially baker's or brewer's yeast, and / or photosynthetic bacteria or non-sulfur adult bacteria, although other combinations of bacteria or the admixture of smaller amounts of such can be used. Almost any amount of effective microorganism can be grown by adding a small amount of organisms to it by adding sugar cane molasses or other nutrient. For the breeding of the effective microorganisms, it may be advantageous to use first a carrier liquid with high sugar cane molasses / nutrient content and to carry out a dilution with water after a sufficient breeding time.
  • a ratio of 1 to 10 may make sense.
  • the EM serve, inter alia, the reinforcement of fermentation processes.
  • the mixing ratio of EM to water to triethylene glycol to sugarcane molasses to saponin for the first material is in the range of 1 to 6 to 10 to 0.005 to 0.03 to 0.3 to 2 to 0.3 to 3, with the entire saponin only after Completion of the EM-breeding is added.
  • a strong reduction of the EM content is possible with a relatively further increase in saponin content, however not preferred. Further dilution with water in a ratio of up to 1 to 10 is also possible.
  • the second substance has a similar composition as the first substance, but still includes water glass, especially soda water glass.
  • water glass especially soda water glass.
  • An example of other technically possible but uneconomical water glasses are potash water glasses. This results in a strong bond, and the treated sludge or the so treated ash solidifies (gradually more or less depending on the proportion of water glass).
  • the treated sludge / ash can thus be used as a building material or be used in large admixture with another building material. This heavy metals are firmly enclosed by the added substance and can not be released by moisture.
  • the second fabric preferably consists of 20% to 60% of the first fabric and 40% to 80% of water glass.
  • a mineral powder of volcanic origin in particular bentonite, can be added in an amount of up to 20%.
  • the accelerating accelerators may include aluminum sulfates and / or resin-based thickeners.
  • This mixture enables effective silicification of the sludge / ash.
  • the method consists in treating the preferably semi-dry or stabilized sludge and / or ash, in particular sewage sludge, with the first substance in the case of use as fertilizer and with the second substance in case of use as building material, in both cases a pretreatment can be carried out .
  • Semi-dry or stabilized sludge is sometimes referred to as fresh or moist sludge, for example, sewage sludge preferably has a moisture content of 25% to 30%.
  • the pretreatment comprises the treatment of the sludge or ash with an effective solution containing microorganisms, which may have a similar composition to the first substance.
  • the treatment itself comprises prolonged standing of the sludge-substance mixture or ash-substance mixture, preferably 1 to 2 weeks. This may be followed by drying, pressing and / or comminution.
  • the mixing ratio of first material to sludge and / or ash is preferably 1 to 4 to 10.
  • the mixing ratio of second material to sludge and / or ash is preferably 2 to 7 to 10.
  • the resulting Material can be used in an admixture of 1 to 6 to 1 to 2 as an admixture in building materials, or the building materials can be added depending on the exact material already before the treatment of the mud / ash.
  • a significantly higher proportion of sludge / ash is possible than in the admixture of the prior art, in which only an admixture of 1 to 10 can be realized.
  • the first substance comprises effective ones Microorganisms, sugar cane molasses, saponins and triethylene glycol, the second substance also sodium silicate and possibly bentonite and / or zeolite and / or talc.
  • An exemplary production process for 50 liters of the first substance comprises the mixture of 5 liters of EM, 38 liters of lukewarm water, 50 ml of triethylene glycol and 2 to 3 liters of sugarcane molasses. The liquid is then stored at room temperature for 2 to 3 weeks. After this time no further multiplication of the microorganisms takes place. Then 5 liters of saponin are added. Further dilution with water in the ratio up to 1 to 10 can take place.
  • This first material can be mixed with sewage sludge (or other sludge and / or ash), preferably fresh or moist sewage sludge having a moisture content (liquid content) of 25% to 30%, preferably in a ratio of 1 to 4 to 10. After further 1 to 2 weeks standing, waiting and / or drying time, the treatment is completed.
  • the treated sewage sludge is odorless and contains no harmful bacteria and can be used due to the high nutrient concentration in principle as a fertilizer.
  • the second substance can be reduced by a mixture of 20 to 60% of this first substance and 40% to 80% of sodium silicate, preferably also the sodium silicate content is reduced by up to a quarter and the equivalent amount of bentonite is added.
  • zeolite and / or talc can be added.
  • sands quartz sands, tuff, volcanic sands, perlites or other materials which have a high reactivity with soda.
  • a hardener of up to 20%, preferably 15%, of the mixture may be added to the resulting mixture, the hardener preferably being aluminum sulfate and / or resin-based Thickener comprises.
  • this second material is mixed in a ratio of 2 to 7 to 10 with sewage sludge (or other sludge and / or ash).
  • the treated sewage sludge is odorless, fire and water resistant and can be used well as a building material or as an admixture with other building materials.
  • mixing with sands, tuff, perlites, bentonites (or zeolite, talc or mixtures of bentonite, zeolite and / or talc), sodium bentonites or calcium bentonites can yield a suitable building material. It can also be mixed with ash, straw, wood waste, hay or spews. The mixing can be done depending on the material with the sewage sludge before the actual treatment.
  • any heavy metals are safely and waterproofly incorporated into the material through the process.
  • 680 ml of the second fabric can be mixed, resulting in a total weight of 1680 grams. After drying remain 696 grams of material, which are odorless, hard, fireproof and waterproof.
  • the method can be carried out in principle based on other sludge, ash or mixtures of ash and ash.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • General Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Health & Medical Sciences (AREA)
  • Biotechnology (AREA)
  • Biochemistry (AREA)
  • Microbiology (AREA)
  • Mechanical Engineering (AREA)
  • Molecular Biology (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Inorganic Chemistry (AREA)
  • Genetics & Genomics (AREA)
  • Zoology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Wood Science & Technology (AREA)
  • Biomedical Technology (AREA)
  • Virology (AREA)
  • Medicinal Chemistry (AREA)
  • General Engineering & Computer Science (AREA)
  • General Health & Medical Sciences (AREA)
  • Fertilizers (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention relates to substances and associated methods, particularly for treating sewage sludge for purposes of commercial utilisation. The sewage sludge is pre-treated with a solution containing effective micro-organisms, dried, comminuted and subsequently mixed with a first substance or a second substance, depending on the desired purpose of use. In order to be able to use the sewage sludge as fertiliser, the first substance contains effective micro-organisms, water, saponins, glycols and sugar cane molasses. For usage as a building material, the second substance also comprises sodium silicate and bentonite in addition to the materials contained in the first substance. Further drying then follows.

Description

Stoffe und Verfahren zur Behandlung von Schlamm oder Asche, insbesondere von  Substances and processes for the treatment of sludge or ash, in particular of
Klärschlamm  sewage sludge
Technisches Gebiet Technical area
Die Erfindung betrifft Stoffe und Verfahren zur Behandlung von Schlämmen oder Aschen oder Mischungen davon, insbesondere von Klärschlamm. Die Erfindung betrifft im Einzelnen Stoffe und Verfahren, die eine Verwendung der Schlämmer und/oder Aschen als Dünger oder Baumaterial ermöglichen. The invention relates to substances and processes for the treatment of sludges or ashes or mixtures thereof, in particular of sewage sludge. More particularly, the invention relates to substances and processes which enable the use of the sludges and / or ashes as fertilizer or building material.
Stand der Technik State of the art
Bei der Abwasserentsorgung fallen große Mengen Klärschlamm an, der zu einem relevanten Teil aus Feststoffen besteht. Zur Mengenreduktion wird der Klärschlamm anaerob in Faultürmen behandelt, wodurch die Feststoffmenge verringert werden kann. Der so entstehende stabilisierte Klärschlamm bietet sich aufgrund des hohen Phosphat- und Nährstoffgehaltes prinzipiell als Dünger an, wobei eine dieser Verwendung entgegenstehende Belastung mit Schwermetallen auch auftreten kann. Nur zu einem kleinen Teil wird der anfallende Klärschlamm für die Düngung verwendet. Der größere Teil muss verbrannt werden. Allerdings hat der stabilisierte Klärschlamm aufgrund des noch hohen Wassergehalts einen schlechten Heizwert, weswegen die Verbrennung energetisch keinen oder kaum Gewinn bringt und deshalb keine Verwertung, sondern eine Kosten verursachende Entsorgung ist. Eine Entsorgung auf einer Deponie ist gesetzlich verboten. Eine Änderung der gesetzlichen Regelungen bezüglich der Verwendung als Dünger kann diesen Verwertungszweck weiter einschränken, was in einigen europäischen Staaten bereits der Fall ist. Klärschlamm kann ebenfalls als Beimischung zu Baumaterial verwendet werden, allerdings kann dabei nur ein Mischungsverhältnis Klärschlamm-Baumaterial von 1 zu 10 oder schlechter realisiert werden, da ansonsten die Stabilität des Baumaterials zu gering wird. Diese Verwendung ist somit ebenfalls nur begrenzt nutzbar. Sewage disposal involves the production of large quantities of sewage sludge, which to a significant extent consists of solids. To reduce the volume of sewage sludge is treated anaerobically in digestion towers, whereby the amount of solids can be reduced. The resulting stabilized sewage sludge is due to the high phosphate and nutrient content in principle as a fertilizer, with a use of this heavy metals can also occur contrary to this use. Only a small part of the sewage sludge is used for the fertilization. The larger part has to be burned. However, the stabilized sewage sludge due to the still high water content has a poor calorific value, which is why the combustion energetically brings little or no profit and therefore no recovery, but a cost-causing disposal. Disposal at a landfill is prohibited by law. A change in the legal regulations regarding the use as fertilizer can further restrict this utilization purpose, which is already the case in some European countries. Sewage sludge can also be used as an admixture to building material, but only a mixing ratio sewage sludge building material of 1 to 10 or worse can be realized, otherwise the stability of the building material is too low. This use is thus also limited use.
Die Möglichkeiten zur Verwertung des Klärschlamms sind somit eingeschränkt und ein hoher Anteil des Klärschlamms muss kostenaufwendig thermisch entsorgt werden. Ähnliches gilt für andere Schlämme, Aschen oder Mischungen von Schlamm und Asche. Deshalb besteht die Notwendigkeit die bisherigen Verwertungsmöglichkeiten dieser Stoffe zu verbessern beziehungsweise neue zu erschließen. The possibilities for recycling the sewage sludge are thus limited and a high proportion of the sewage sludge must be disposed of costly thermally. The same applies to other sludges, ashes or mixtures of mud and ash. Therefore, there is a need to improve the previous utilization possibilities of these substances or to develop new ones.
Aufgabe der Erfindung Object of the invention
Die Aufgabe der Erfindung liegt darin, Stoffe und Verfahren bereitzustellen, um die Verwertung von Schlämmen und/oder Aschen als Dünger zu verbessern und den Einsatz als Baumaterial zu ermöglichen. The object of the invention is to provide substances and methods to improve the utilization of sludges and / or ashes as fertilizer and to enable use as a building material.
Technische Lösung Diese Aufgabe wird gelöst durch einen ersten Stoff nach Anspruch 1 oder einen zweiten Stoff nach Anspruch 4 sowie einem Verfahren nach Anspruch 9 unter Verwendung des ersten Stoffes oder des zweiten Stoffes. Vorteilhafte Ausführungsformen sind Gegenstand der Unteransprüche. Der erste Stoff umfasst effektive Mikroorganismen (EM), Wasser und desinfizierende und/oder Geruchs neutralisierende Chemikalien. Bei letzteren handelt es sich bevorzugt um Saponine und Glykole, insbesondere Triethylenglykol. Des Weiteren kann auch Zuckerrohrmelasse oder ein anderer Nährstoff für Bakterien zugefügt werden, um die Lebensdauer der effektiven Mikroorganismen geeignet zu steuern. Ebenfalls kann durch eine Zeit der Lagerung mit Hilfe von Zuckerrohrmelasse oder anderer Nährstoffe eine Vermehrung der Organismen (EM-Zucht) abgewartet werden und das Saponin oder andere Chemikalien ganz oder teilweise erst danach hinzugegeben werden. Technical Solution This object is achieved by a first fabric according to claim 1 or a second fabric according to claim 4 and a process according to claim 9 using the first fabric or the second fabric. Advantageous embodiments are the subject of the dependent claims. The first substance includes effective microorganisms (EM), water and disinfecting and / or odor neutralizing chemicals. The latter are preferably saponins and glycols, in particular triethylene glycol. Furthermore, sugarcane molasses or other nutrient for bacteria may also be added to properly control the life of the effective microorganisms. Likewise, through a period of storage with the help of sugar cane molasses or other nutrients, an increase in the number of organisms (EM breeding) can be awaited and the saponin or other chemicals can be added wholly or partially afterwards.
Beispiele für mögliche Saponine sind Aglykone, insbesondere Steroidsaponine, Steoridalkaloidsaponine und/oder Triterpensaponine. Die Saponine können auch natürlichen Ursprungs sein, wie beispielsweise aus Waschnuss. Technisch mögliche aber nicht bevorzugte Alternativen zu Triethylenglykol sind Cyclodextrine. Examples of possible saponins are aglycones, in particular steroid saponins, steroid alkaloid saponins and / or triterpene saponins. The saponins may also be of natural origin, such as from soapnut. Technically possible but not preferred alternatives to triethylene glycol are cyclodextrins.
Bei effektiven Mikroorganismen handelt es sich üblicherweise um eine Mischung verschiedener natürlich vorkommender Mikroorganismen. Am häufigsten ist ein großer Anteil an Milchsäurebakterien, Hefen, insbesondere Back- oder Bierhefe, und/oder Photosynthesebakterien bzw. Nichtschwefelpurpurbakterien, wobei auch andere Bakterienkombinationen oder die Beimischung kleinerer Mengen solcher verwendet werden können. Nahezu beliebige Mengen effektiver Mikroorganismen können mit Hilfe einer kleinen Ausgangsmenge an Organismen durch Zugabe von Zuckerrohrmelasse oder einem anderen Nährstoff gezüchtet werden. Für die Zucht der effektiven Mikroorganismen kann es vorteilhaft sein, zuerst eine Trägerflüssigkeit mit hohem Zuckerrohrmelasse/Nährstoffanteil zu verwenden und nach ausreichender Zuchtzeit eine Verdünnung mit Wasser durchzuführen. Je nach Zusammensetzung kann ein Verhältnis 1 zu 10 sinnvoll sein. Bei der Anwendung im Rahmen dieser Erfindung dienen die EM unter anderem der Verstärkung von Gärungsprozessen. Bevorzugt ist das Misch Verhältnis EM zu Wasser zu Triethylenglykol zu Zuckerrohrmelasse zu Saponin für den ersten Stoff im Bereich 1 zu 6 bis 10 zu 0,005 bis 0,03 zu 0,3 bis 2 zu 0,3 bis 3, wobei das gesamte Saponin erst nach Abschluss der EM-Zucht hinzugegeben wird. Technisch ist eine starke Verringerung des EM-Anteils bei einer relativ gesehen weiteren Vergrößerung Saponin-Anteils möglich, allerdings nicht bevorzugt. Eine weitere Verdünnung mit Wasser im Verhältnis bis zu 1 zu 10 ist ebenfalls möglich. Effective microorganisms are usually a mixture of various naturally occurring microorganisms. The most common is a large proportion of lactic acid bacteria, yeasts, especially baker's or brewer's yeast, and / or photosynthetic bacteria or non-sulfur adult bacteria, although other combinations of bacteria or the admixture of smaller amounts of such can be used. Almost any amount of effective microorganism can be grown by adding a small amount of organisms to it by adding sugar cane molasses or other nutrient. For the breeding of the effective microorganisms, it may be advantageous to use first a carrier liquid with high sugar cane molasses / nutrient content and to carry out a dilution with water after a sufficient breeding time. Depending on the composition, a ratio of 1 to 10 may make sense. When used in the context of this invention, the EM serve, inter alia, the reinforcement of fermentation processes. Preferably, the mixing ratio of EM to water to triethylene glycol to sugarcane molasses to saponin for the first material is in the range of 1 to 6 to 10 to 0.005 to 0.03 to 0.3 to 2 to 0.3 to 3, with the entire saponin only after Completion of the EM-breeding is added. Technically, a strong reduction of the EM content is possible with a relatively further increase in saponin content, however not preferred. Further dilution with water in a ratio of up to 1 to 10 is also possible.
Durch Hinzufügen des ersten Stoffes zu Schlamm und/oder Asche und/oder Mischungen davon werden schädliche und/oder stark riechende Bakterien kostengünstig beseitigt, wodurch der so behandelte Schlamm bzw. die so behandelte Asche bzw. Schlamm-Asche-Mischung als Dünger verwendbar ist. Dabei genügt es, auf 10 Einheiten Schlamm/Asche 1 bis 4 Einheiten des ersten Stoffes hinzuzugeben, um eine Verwendung als Dünger zu ermöglichen. Durch die Anwendung wird ebenfalls der pH- Wert zu für die Landwirtschaft günstigeren Werten hin verändert. By adding the first substance to sludge and / or ash and / or mixtures thereof harmful and / or strong-smelling bacteria are inexpensively eliminated, whereby the thus treated sludge or the so-treated ash or sludge-ash mixture is used as fertilizer. It is sufficient to add 10 units of sludge / ash 1 to 4 units of the first substance to allow use as fertilizer. The application also changes the pH to more favorable for agriculture.
Der zweite Stoff hat eine ähnliche Zusammensetzung wie der erste Stoff, umfasst allerdings noch Wasserglas, insbesondere Natronwasserglas. Ein Beispiel für weitere technisch mögliche aber unwirtschaftliche Wassergläser sind Kaliwassergläser. Dadurch ergibt sich eine feste Bindung, und der behandelte Schlamm bzw. die so behandelte Asche verfestigt sich (graduell je nach Anteil an Wasserglas mehr oder weniger). Der behandelte Schlamm/Asche kann somit als Baumaterial verwendet beziehungsweise in großer Beimischung zu einem anderen Baumaterial verwertet werden. Dabei werden Schwermetalle von dem zugegebenen Stoff fest eingeschlossen und können auch durch Feuchtigkeit nicht mehr freigesetzt werden. Der zweite Stoff besteht bevorzugt zu 20 % bis 60% aus dem ersten Stoff und 40% bis 80% aus Wasserglas. Ferner kann ein mineralisches Pulver vulkanischen Ursprungs, insbesondere Bentonit, in einem Anteil von bis zu 20% beigegeben werden. Ebenfalls können zusätzliche Stoffe zur Beschleunigung der Aushärtung zugegeben werden, hierbei sind Zusatzstoffanteile bis 15% bevorzugt, die Stoffe zur Beschleunigung der Aushärtung können Aluminiumsulfate und/oder auf Kunstharz basierende Verdickungsmittel umfassen. Durch diese Mischung wird eine effektive Verkieselung des Schlamms/der Asche ermöglicht. Das Verfahren besteht im Behandeln des bevorzugt halbtrockenen oder stabilisierten Schlamms und/oder Asche, insbesondere Klärschlamms, mit dem ersten Stoff im Falle der Verwendung als Dünger und mit dem zweiten Stoff im Fall der Verwendung als Baumaterial, wobei in beiden Fällen eine Vorbehandlung durchgeführt werden kann. Halbtrockener oder stabilisierter Schlamm wird teilweise auch als frischer bzw. feuchter Schlamm bezeichnet, bevorzugt hat beispielsweise Klärschlamm einen Feuchtigkeitsanteil von 25% bis 30%. Die Vorbehandlung umfasst die Behandlung des Schlamms bzw. der Asche mit einer effektive Mikroorganismen enthaltenden Lösung, welche eine ähnliche Zusammensetzung wie der erste Stoff aufweisen kann. Die Behandlung selbst umfasst ein längeres Stehen der Schlamm-Stoff-Mischung bzw. Asche-Stoff Mischung, bevorzugt 1 bis 2 Wochen. Daran schließt sich eventuell eine Trocknung, eine Pressung und/oder eine Zerkleinerung an. The second substance has a similar composition as the first substance, but still includes water glass, especially soda water glass. An example of other technically possible but uneconomical water glasses are potash water glasses. This results in a strong bond, and the treated sludge or the so treated ash solidifies (gradually more or less depending on the proportion of water glass). The treated sludge / ash can thus be used as a building material or be used in large admixture with another building material. This heavy metals are firmly enclosed by the added substance and can not be released by moisture. The second fabric preferably consists of 20% to 60% of the first fabric and 40% to 80% of water glass. Furthermore, a mineral powder of volcanic origin, in particular bentonite, can be added in an amount of up to 20%. Also, additional materials may be added to accelerate cure, with additive levels of up to 15% being preferred, the accelerating accelerators may include aluminum sulfates and / or resin-based thickeners. This mixture enables effective silicification of the sludge / ash. The method consists in treating the preferably semi-dry or stabilized sludge and / or ash, in particular sewage sludge, with the first substance in the case of use as fertilizer and with the second substance in case of use as building material, in both cases a pretreatment can be carried out , Semi-dry or stabilized sludge is sometimes referred to as fresh or moist sludge, for example, sewage sludge preferably has a moisture content of 25% to 30%. The pretreatment comprises the treatment of the sludge or ash with an effective solution containing microorganisms, which may have a similar composition to the first substance. The treatment itself comprises prolonged standing of the sludge-substance mixture or ash-substance mixture, preferably 1 to 2 weeks. This may be followed by drying, pressing and / or comminution.
Im Falle der Verwendung als Dünger ist das Mischungsverhältnis erster Stoff zu Schlamm und/oder Asche bevorzugt 1 bis 4 zu 10. Im Falle der Verwendung als Baumaterial ist das Mischungsverhältnis zweiter Stoff zu Schlamm und/oder Asche bevorzugt 2 bis 7 zu 10. Das resultierende Material kann in einer Beimischung von 1 zu 6 bis 1 zu 2 als Beimischung in Baumaterialien verwendet werden, bzw. können die Baumaterialien je nach genauem Material bereits vor der Behandlung dem Schlamm/der Asche hinzugefügt werden. Somit ist bei der Verwendung als Baustoff ein erheblich höherer Schlamm-/Ascheanteil möglich als bei der Beimischung nach Stand der Technik, bei dem nur eine Beimischung von 1 zu 10 realisierbar ist. In the case of use as a fertilizer, the mixing ratio of first material to sludge and / or ash is preferably 1 to 4 to 10. In the case of use as a building material, the mixing ratio of second material to sludge and / or ash is preferably 2 to 7 to 10. The resulting Material can be used in an admixture of 1 to 6 to 1 to 2 as an admixture in building materials, or the building materials can be added depending on the exact material already before the treatment of the mud / ash. Thus, when used as a building material, a significantly higher proportion of sludge / ash is possible than in the admixture of the prior art, in which only an admixture of 1 to 10 can be realized.
Als abschließender Schritt kann eine erneute Trocknung und/oder Zerkleinerung/ein Zurechtschneiden erfolgen, je nach Verwendungszweck. As a final step, re-drying and / or comminution / trimming can take place, depending on the intended use.
Beschreibung bevorzugter Ausführungsformen bevorzugten Ausführungsformen umfasst der erste Stoff effektive Mikroorganismen, Zuckerrohrmelasse, Saponine und Triethylenglykol, der zweite Stoff dazu noch Natronwasserglas und eventuell Bentonit und/oder Zeolith und/oder Talk. Ein beispielhaftes Herstellungsverfahren für 50 Liter des ersten Stoffes umfasst die Mischung von 5 Litern EM, 38 Litern lauwarmes Wasser, 50 ml Triethylenglykol und 2 bis 3 Liter Zuckerrohrmelasse. Die Flüssigkeit wird anschließend bei Zimmertemperatur 2 bis 3 Wochen gelagert. Nach dieser Zeit findet keine weitere Vermehrung der Mikroorganismen statt. Dann werden 5 Liter Saponin hinzugefügt. Eine weitere Verdünnung mit Wasser im Verhältnis bis zu 1 zu 10 kann erfolgen. DESCRIPTION OF PREFERRED EMBODIMENTS Preferred Embodiments The first substance comprises effective ones Microorganisms, sugar cane molasses, saponins and triethylene glycol, the second substance also sodium silicate and possibly bentonite and / or zeolite and / or talc. An exemplary production process for 50 liters of the first substance comprises the mixture of 5 liters of EM, 38 liters of lukewarm water, 50 ml of triethylene glycol and 2 to 3 liters of sugarcane molasses. The liquid is then stored at room temperature for 2 to 3 weeks. After this time no further multiplication of the microorganisms takes place. Then 5 liters of saponin are added. Further dilution with water in the ratio up to 1 to 10 can take place.
Dieser erste Stoff kann mit Klärschlamm (oder anderen Schlämmen und/oder Asche), bevorzugt frischer bzw. feuchter Klärschlamm mit einem Feuchtigkeitsanteil (Flüssiganteil) von 25% bis 30%, vermischt werden, bevorzugt in einem Verhältnis 1 bis 4 zu 10. Nach weiteren 1 bis 2 Wochen Steh-, Warte- und/oder Trockenzeit ist die Behandlung abgeschlossen. Der behandelte Klärschlamm ist geruchsneutral und enthält keine schädlichen Bakterien und kann augrund der hohen Nährstoffkonzentration prinzipiell als Dünger eingesetzt werden. Alternativ zum ersten Stoff kann der zweite Stoff durch eine Mischung von 20 bis 60% dieses ersten Stoffes und 40% bis 80% von Natronwasserglas, wobei bevorzugt auch der Natronwasserglasanteil um bis zu einem Viertel verringert wird und die äquivalente Menge Bentonit hinzugegeben wird. Statt Bentonit kann teilweise oder vollständig Zeolith und/oder Talk hinzugefügt werden. Nicht bevorzugt, aber technisch möglich ist die Verwendung von Sanden, Quarzsanden, Tuffgestein, vulkanischen Sande, Perlite oder andere Materialien, die eine hohe Reaktivität mit Natron aufweisen. Ferner kann der resultierenden Mischung ein Härter im Umfang von bis zu 20%, bevorzugt 15%, der Mischung hinzugegeben werden, wobei der Härter bevorzugt Aluminiumsulfat und/oder auf Kunstharz basierende Verdickungsmittel umfasst. Anschließend wird dieser zweite Stoff im Verhältnis von 2 bis 7 zu 10 mit Klärschlamm (oder anderen Schlämmen und/oder Asche) vermischt. Nach einer geeigneten Trocknungszeit, bei der sich das Gewicht durch Verdunsten des Wassers um etwa 2/3 reduziert, ist der behandelte Klärschlamm geruchsneutral, feuerfest und wasserfest und kann gut als Baumaterial oder als Beimischung zu anderen Baumaterialien verwendet werden. Beispielsweise kann je nach Anwendung die Vermischung mit Sanden, Tuffgestein, Perliten, Bentoniten (bzw. Zeolith, Talk oder Mischungen aus Bentonit, Zeolith und/oder Talk), Natriumbentoniten oder Calciumbentoniten ein geeignetes Baumaterial ergeben. Ebenfalls kann eine Vermischung mit Asche, Stroh, Holzabfällen, Heu oder Spuckstoffen erfolgen. Die Vermischung kann je nach Material mit dem Klärschlamm vor der eigentlichen Behandlung erfolgen. Wichtig ist vor allem, dass durch das Verfahren eventuelle Schwermetalle sicher und wasserfest im Material eingebunden werden. Beispielsweise können zu 1000 Gramm feuchten Klärschlamm 680 ml des zweiten Stoffes gemischt werden, womit sich ein Gesamtgewicht von 1680 Gramm ergibt. Nach Trocknung verbleiben 696 Gramm Material, welche Geruchsneutral, hart, feuerfest und wasserfest sind. Das Verfahren kann prinzipiell auf Basis auch anderer Schlämme, Asche oder Mischungen aus Schamm und Asche durchgeführt werden. This first material can be mixed with sewage sludge (or other sludge and / or ash), preferably fresh or moist sewage sludge having a moisture content (liquid content) of 25% to 30%, preferably in a ratio of 1 to 4 to 10. After further 1 to 2 weeks standing, waiting and / or drying time, the treatment is completed. The treated sewage sludge is odorless and contains no harmful bacteria and can be used due to the high nutrient concentration in principle as a fertilizer. As an alternative to the first substance, the second substance can be reduced by a mixture of 20 to 60% of this first substance and 40% to 80% of sodium silicate, preferably also the sodium silicate content is reduced by up to a quarter and the equivalent amount of bentonite is added. Instead of bentonite, partially or completely zeolite and / or talc can be added. Not preferred, but technically possible is the use of sands, quartz sands, tuff, volcanic sands, perlites or other materials which have a high reactivity with soda. Further, a hardener of up to 20%, preferably 15%, of the mixture may be added to the resulting mixture, the hardener preferably being aluminum sulfate and / or resin-based Thickener comprises. Subsequently, this second material is mixed in a ratio of 2 to 7 to 10 with sewage sludge (or other sludge and / or ash). After a suitable drying time, during which the weight is reduced by evaporation of the water by about 2/3, the treated sewage sludge is odorless, fire and water resistant and can be used well as a building material or as an admixture with other building materials. For example, depending on the application, mixing with sands, tuff, perlites, bentonites (or zeolite, talc or mixtures of bentonite, zeolite and / or talc), sodium bentonites or calcium bentonites can yield a suitable building material. It can also be mixed with ash, straw, wood waste, hay or spews. The mixing can be done depending on the material with the sewage sludge before the actual treatment. Above all, it is important that any heavy metals are safely and waterproofly incorporated into the material through the process. For example, to 1000 grams of wet sewage sludge, 680 ml of the second fabric can be mixed, resulting in a total weight of 1680 grams. After drying remain 696 grams of material, which are odorless, hard, fireproof and waterproof. The method can be carried out in principle based on other sludge, ash or mixtures of ash and ash.
Obwohl die vorliegende Erfindung anhand der beigefügten Ausführungsbeispiele detailliert beschrieben worden ist, ist für den Fachmann selbstverständlich, dass die Erfindung nicht auf diese Ausführungsformen beschränkt ist, sondern vielmehr Abwandlungen oder Änderungen gemäß der beigefügten Ansprüche umfasst, wobei die Änderungen durch unterschiedliche Kombinationen einzelner dargestellter Merkmale als auch durch Weglassen einzelner Merkmale erfolgen können. Insbesondere ist jegliche Kombination der dargestellten Merkmale von der Erfindung umfasst. Although the present invention has been described in detail with reference to the accompanying embodiments, it will be understood by those skilled in the art that the invention is not limited to these embodiments, but rather modifications or changes according to the appended claims, the changes by different combinations of individual illustrated features can also be done by omitting individual features. In particular, any combination of the illustrated features of the invention includes.

Claims

Ansprüche claims
1. Stoff zur Behandlung von Schlamm und/oder Asche, insbesondere von Klärschlamm, der umfasst: 1. A substance for the treatment of sludge and / or ash, in particular sewage sludge, comprising:
- effektive Mikroorganismen;  - effective microorganisms;
- Wasser; und  - Water; and
wenigstens eine desinfizierende und/oder geruchsneutralisierende at least one disinfecting and / or odor-neutralizing
Chemikalie. Chemical.
2. Stoff nach Anspruch 1, wobei die desinfizierenden und/oder geruchsneutralisierenden Chemikalien Saponine und/oder Glykole umfassen. A fabric according to claim 1, wherein the disinfecting and / or odor-neutralizing chemicals comprise saponins and / or glycols.
3. Stoff nach Anspruch 2, wobei der Stoff ferner Nährstoffe für Bakterien, insbesondere Zuckerrohrmelasse, umfasst. The fabric of claim 2, wherein the fabric further comprises nutrients for bacteria, especially sugarcane molasses.
4. Stoff nach Anspruch 3, wobei der Stoff eine Einheit effektive Mikroorganismen, 6 bis 10 Einheiten Wasser, 0,005 bis 0,03 Einheiten Trienthylglykol, 0,3 bis 2 Einheiten Zuckerrohrmelasse und 0,3 bis 3 Einheiten Saponin enthält. A fabric according to claim 3, wherein said fabric contains one unit of effective microorganisms, 6 to 10 units of water, 0.005 to 0.03 units of triethyl glycol, 0.3 to 2 units of sucrose molasses, and 0.3 to 3 units of saponin.
5. Stoff zur Behandlung von Schlamm und/oder Asche, insbesondere von Klärschlamm, der umfasst: 5. A substance for the treatment of sludge and / or ash, in particular sewage sludge, comprising:
- einen ersten Stoff nach einem der vorherigen Ansprüche, und  a first substance according to one of the preceding claims, and
- Wasserglas, insbesondere Natronwasserglas.  - Water glass, in particular soda water glass.
6. Stoff nach Anspruch 5, wobei der erste Stoff 20% bis 60% des zweiten Stoffes ausmacht und der Anteil an Wasserglas 40% bis 80% des zweiten Stoffes ausmacht. The fabric of claim 5, wherein the first fabric is from 20% to 60% of the second fabric and the content of water glass is from 40% to 80% of the second fabric.
7. Stoff nach Ansprüchen 5 oder 6, der ferner mineralisches Pulver vulkanischen Ursprungs, insbesondere Bentonit und/oder Zeolith und/oder Talk, umfasst. 7. A fabric according to claims 5 or 6, further comprising mineral powder of volcanic origin, in particular bentonite and / or zeolite and / or talc.
8. Stoff nach Anspruch 7, wobei der Anteil an Bentonit bzw. Zeolith bzw. Talk bis zu 20% des Stoffes ausmacht. 8. A fabric according to claim 7, wherein the proportion of bentonite or zeolite or talc accounts for up to 20% of the substance.
9. Verfahren zur Behandlung von Schlamm und/oder Asche, insbesondere von Klärschlamm, zum Zweck der Verwertung, dadurch gekennzeichnet, dass zu vorbehandeltem oder nicht vorbehandeltem Schlamm bzw. Asche ein erster Stoff nach einem der Ansprüche 1 bis 4 oder ein zweiter Stoff nach einem der Ansprüche 5 bis 8 hinzugegeben wird. 9. A method for the treatment of sludge and / or ash, in particular of sewage sludge, for the purpose of utilization, characterized in that pretreated or not pretreated sludge or ash, a first substance according to one of claims 1 to 4 or a second substance after a of claims 5 to 8 is added.
10. Verfahren nach Anspruch 9, dadurch gekennzeichnet, dass der Schlamm bzw. die Asche bei einer Vorbehandlung mit einer effektive Mikroorganismen enthaltenden Lösung behandelt wird. 10. The method according to claim 9, characterized in that the sludge or the ash is treated in a pretreatment with an effective solution containing microorganisms.
11. Verfahren nach Anspruch 9 oder 10, dadurch gekennzeichnet, dass auf 10 Einheiten Schlamm bzw. Asche 1 bis 4 Einheiten des ersten Stoffes kommen. 11. The method according to claim 9 or 10, characterized in that come to 10 units of sludge or ash 1 to 4 units of the first substance.
12. Verfahren nach Anspruch 9 oder 10, dadurch gekennzeichnet, dass auf 10 Einheiten Schlamm bzw. Asche 2 bis 7 Einheiten des zweiten Stoffes kommen. 12. The method according to claim 9 or 10, characterized in that come to 10 units of sludge or ash 2 to 7 units of the second material.
13. Verfahren nach einem der Ansprüche 9 bis 12, dadurch gekennzeichnet, dass der Schlamm bzw. die Asche vor der Vorbehandlung oder der Zugabe des ersten oder zweiten Stoffs halbtrocken oder stabilisiert ist, bevorzugt mit einem Feuchtigkeitsanteil zwischen 25% und 30%. 13. The method according to any one of claims 9 to 12, characterized in that the sludge or the ashes before the pretreatment or the addition of the first or second substance is semi-dry or stabilized, preferably with a moisture content of between 25% and 30%.
14. Verfahren nach einem der Ansprüche 9 bis 13, dadurch gekennzeichnet, dass nach Zugabe des ersten oder zweiten Stoffes eine weitere Trocknung und/oder eine Pressung und/oder im Falle des zweiten Stoffes die Zugabe von Härtern mit bis zu 20%, bevorzugt 10%, Stoffanteil in einer geeigneten Reihenfolge erfolgen, wobei die Härter bevorzugt Aluminiumsulfate und/oder auf Kunstharz basierende Verdickungsmittel umfassen. 14. The method according to any one of claims 9 to 13, characterized in that after addition of the first or second substance further drying and / or pressing and / or in the case of the second substance, the addition of hardeners with up to 20%, preferably 10 %, Substance content in a suitable order, wherein the Hardeners preferably comprise aluminum sulphates and / or thickeners based on synthetic resin.
15. Verfahren nach einem der Ansprüche 9 bis 14, dadurch gekennzeichnet, dass der Schlamm bzw. die Asche vor der Vorbehandlung oder der Zugabe des ersten oder zweiten Stoffs bzw. danach mit einem Material und/oder Baumaterial vermischt werden, bevorzugt so, dass in der Mischung am Ende des Verfahrens der Material-/Baumaterialanteil unter 90%, insbesondere unter 60% liegt. 15. The method according to any one of claims 9 to 14, characterized in that the sludge or the ash before the pretreatment or the addition of the first or second substance or thereafter with a material and / or building material are mixed, preferably such that in the mixture at the end of the process, the material / building material content is less than 90%, in particular less than 60%.
PCT/EP2012/072147 2011-11-08 2012-11-08 Substances and methods for treating sludge or ash, in particular sewage sludge WO2013068468A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE102011055144.1 2011-11-08
DE102011055144A DE102011055144A1 (en) 2011-11-08 2011-11-08 Substances and processes for the treatment of sewage sludge

Publications (1)

Publication Number Publication Date
WO2013068468A1 true WO2013068468A1 (en) 2013-05-16

Family

ID=47297126

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/EP2012/072147 WO2013068468A1 (en) 2011-11-08 2012-11-08 Substances and methods for treating sludge or ash, in particular sewage sludge

Country Status (2)

Country Link
DE (2) DE202011110704U1 (en)
WO (1) WO2013068468A1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2017125464A1 (en) 2016-01-19 2017-07-27 Schweighofer Thomas Josef Cleaning agent comprising saponin and lactic acid bacteria

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110651683B (en) * 2019-09-24 2021-08-27 柳州市农业科学研究所 Light simple matrix seedling raising method for sugarcane seedlings

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003112166A (en) * 2001-09-30 2003-04-15 Eiichi Tashiro Anaerobic cleaning method for soil
JP2006231209A (en) * 2005-02-25 2006-09-07 Aquas Corp Waste water treatment method
JP2007313407A (en) * 2006-05-24 2007-12-06 Natoo Kenkyusho:Kk Multifunctional modifier, non-heating modification treatment method and pollution-free plant growing material

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003112166A (en) * 2001-09-30 2003-04-15 Eiichi Tashiro Anaerobic cleaning method for soil
JP2006231209A (en) * 2005-02-25 2006-09-07 Aquas Corp Waste water treatment method
JP2007313407A (en) * 2006-05-24 2007-12-06 Natoo Kenkyusho:Kk Multifunctional modifier, non-heating modification treatment method and pollution-free plant growing material

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
DATABASE WPI Week 200360, Derwent World Patents Index; AN 2003-630152, XP002691526 *
DATABASE WPI Week 200663, Derwent World Patents Index; AN 2006-606964, XP002691525 *
DATABASE WPI Week 200841, Derwent World Patents Index; AN 2008-G43111, XP002691524 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2017125464A1 (en) 2016-01-19 2017-07-27 Schweighofer Thomas Josef Cleaning agent comprising saponin and lactic acid bacteria

Also Published As

Publication number Publication date
DE202011110704U1 (en) 2015-09-11
DE102011055144A1 (en) 2013-05-08

Similar Documents

Publication Publication Date Title
EP0573478B1 (en) Process for separate treatment and disposal of mixtures of solid and liquid organic waste materials
DE102008050349B4 (en) Process for the precipitation of phosphorus from phosphate-contaminated wastewater
EP3681851A1 (en) Process for the production of humic substances from biomass such as wood, bark, cereal straw, leaves, herbaceous plants and also tree fungi, sewage sludge and other organic wastes
WO2009021528A1 (en) Method for the production of humus- and nutrient-rich and water-storing soils or soil substrates for sustainable land use and development systems
EP3233759B1 (en) Method for producing nutrient-rich soils or soil substrates
WO2016116099A2 (en) Soil auxiliary substances and method for their preparation and their use
EP1577269A1 (en) Zeolite in biogas winning
EP2576449A1 (en) Mixture for reducing the formation of magnesium ammonium phosphate (struvite) in clarification plants
DE102015100644A1 (en) Production of a liquid soil additive based on humic and fulvic acids for use as soil and water adjuvant to positively influence the soil-water-plant-nutrient balance
EP3326992A1 (en) Method for the treatment of manure slurry and fermentation waste with materials containing humic acids
WO2013068468A1 (en) Substances and methods for treating sludge or ash, in particular sewage sludge
WO2011060904A1 (en) Method for producing soil additives for improving the cationic exchange capacity, the nutrition and the water retention capacity of soils
DE102014119248A1 (en) Process for the production of nutrient-rich soils or soil substrates
DE102012007900B4 (en) Process for the treatment of organic waste, in particular digestate from biogas plants
DE102013217080B4 (en) Fertilizer pellet and process for its preparation
DE4240807C1 (en) Fertilisers based on dewatered sludge mixt. - contains sewage sludge ash and mineral fertiliser releasing nutrients according to need
DE10120372A1 (en) Liquid and/or solid, nitrogen-containing organic fertilizer, obtained by reacting humus, humic acid or its salt and manure
DE19644613C2 (en) Process for the production of a fertilizer using liquid manure
DE3826873A1 (en) Process for the preparation of fertiliser from impregnated (saturated) used paper shreds
DE4037113A1 (en) BIOLOGICAL FLOOR AUXILIARY AGENT FOR AGRICULTURAL PURPOSES AND METHOD FOR THE PRODUCTION THEREOF
DE102013010007B4 (en) A method for separating a suspension, products produced thereafter and the use thereof
DE102015100645A1 (en) Production of a free-flowing soil additive based on liquid humic and fulvic acids, as well as solid inorganic and organic substance for use as soil and water additive to positively influence the soil-water-plant-nutrient balance
EP0936204B1 (en) Method of producing compost fertiliser substrates
DE19880157B4 (en) A method of preparing a microorganism mixture for binding atmospheric nitrogen, increasing the solubility of phosphorus compounds and decomposing food oil sediment and said mixture
AT509287B1 (en) FILTER SUBSTRATE FOR THE BIOLOGICAL PREPARATION OF PURE WATER AND METHOD FOR THE PRODUCTION THEREOF

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 12797743

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: DE

122 Ep: pct application non-entry in european phase

Ref document number: 12797743

Country of ref document: EP

Kind code of ref document: A1