EP3174831A1 - Method and device for treating liquid manure and fermentation remains - Google Patents
Method and device for treating liquid manure and fermentation remainsInfo
- Publication number
- EP3174831A1 EP3174831A1 EP15745148.5A EP15745148A EP3174831A1 EP 3174831 A1 EP3174831 A1 EP 3174831A1 EP 15745148 A EP15745148 A EP 15745148A EP 3174831 A1 EP3174831 A1 EP 3174831A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- precipitation
- manure
- digestate
- container
- phase
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Withdrawn
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01C—PLANTING; SOWING; FERTILISING
- A01C3/00—Treating manure; Manuring
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/40—Treatment of liquids or slurries
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/50—Treatments combining two or more different biological or biochemical treatments, e.g. anaerobic and aerobic treatment or vermicomposting and aerobic treatment
-
- 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
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/4618—Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water
- C02F2001/46185—Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water only anodic or acidic water, e.g. for oxidizing or sterilizing
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/02—Fluid flow conditions
- C02F2301/024—Turbulent
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/02—Fluid flow conditions
- C02F2301/026—Spiral, helicoidal, radial
-
- 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
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Definitions
- the invention relates to a method and a device for the treatment of agricultural manure and
- Digesting in which the manure or the digestate- a precipitant added, and then with water as a release agent in a ⁇ bsetz effectnis a thick or flake phase of a clear or thin phase
- agricultural manure should comprise all feces from animal husbandry, including manure.
- fermentation residues should also be precipitated in the invention. Fermentation residues include fermentation residues
- Biogas plants fermentation residues from the ethanol production, as well as fermentation residues from the food and food production, seepage juices from silage facilities and digestate storage facilities.
- Agricultural manure in a thick or flake phase and in a thin or clear phase often creates the problem of adequate separation of said flake phase from the clear phase.
- the flakes are very Fragile and form in the precipitation, among other things, from dissolved ingredients of manure or digestate. Since the chemical precipitation with the addition of precipitant is relatively fast, it also depends on the
- the invention is therefore based on the object, a method, and a device of the generic type to the effect that the so-called precipitation and separation of manure or digestate in a flock or thick phase and in a clear or thin phase much faster and more effective, and for the flakes formed by precipitation runs gently.
- the core of the method according to the invention is that the settling tank is preceded by a precipitation vessel to be filled from bottom to top into which the liquid manure or fermentation residue is introduced at the bottom and swirling, and also with a precipitating agent directly on the bottom side directly into said turbulence of the introduced liquid manure or digestate is injected, such that the mixture of manure or digestate together with the injected precipitant in the precipitation container is ascending and expanding so that it flows out of the top of the precipitation vessel and into the
- Vortex but as will be further illustrated, the vortex remains limited to the point of introduction.
- the precipitation reaction proceeds extremely fast, i. in a few seconds or even less than a second.
- the flocs produced by the precipitation float upwards as foam. It can be seen that the manure only rotates near the bottom of the precipitation tank, but above the foam floats up completely without rotation, and expands from the
- constant rotation can be generated, for example, by an introduction of the manure by these eccentric, i. to the vertical central axis of the upright
- Precipitation container is introduced eccentrically.
- Acidified water is thus said anolyte or a mixture of anolyte and water.
- iron and iron compounds such as
- Iron hydroxide arise, which are of considerable advantage in a post-fermentation of the thick or flake phase in a Nachvergärungs drove a biogas plant, because they support the gas drive.
- to acidify the water may also be acetic acid, or propionic acid, or sulfurous acid, or
- Citric acid or lactic acid can be used.
- the advantage of these variants is that these too in a return of the flocculent or thick phase in a fermentation room or Nachvergär syndromem a biogas plant the Support biogas-driving microbiology.
- the said acidic anolyte acts thereby chemically so by, among other things, with the iron-containing
- Hemoglobin disintegrates from the animal manure in the same precipitate. This in the way that the amount of the required said precipitating agent is thereby reduced.
- a predetermined amount of water is presented, and said, transferred from the precipitator mixture from the top of the introduced water to separate the thick or flake phase of the thin or clear phase.
- the settling tank expands the floating
- the precipitation container is an upright
- cylindrical container is, and that said
- said turbulence may be generated by a rotating element. This is a
- Manure / digestate But it can also be done together with the eccentric introduction of manure / digestate, if it is, for example, very heavy gullies / fermentation residues with a higher content of dry matter.
- the settling in the settling flocculent or thick phase forming can be removed by skimming or pushing off, and the remaining thin or clear phase be further clarified by the addition of milk of lime or dilute potassium hydroxide solution and withdrawn as nutrient for plant crops.
- Injection points of the precipitation container is or can be initiated, which are arranged at different heights, measured from the bottom of the precipitation container, such that the effectiveness of the precipitation different rotational speeds and / or
- Viscosities of different gullies to be precipitated is customizable.
- the speed of rotation depends on the diameter of the precipitation tank and the pumping capacity with which the liquid manure or the fermentation residues in the
- a further optional inlet opening of liquid manure and / or water and / or anolyte and / or catholyte and / or precipitant is provided in the bottom of the precipitation vessel, via which without rotation of one of said media can be introduced.
- the settling tank is preceded by a precipitation tank, which is to be filled from bottom to top, in which the liquid manure or fermentation residues can be introduced at the bottom by means of an inlet flange, and also directly into the said turbulence of the introduced bottom side
- a precipitant is continuously injected through an injection with such a way that the mixture of manure or digestate together with the injected precipitant in the precipitation container is ascending and expanding upwards so that it flows out of the top of the precipitation container from a discharge and in the settling container can be introduced.
- Flake foam rotates or turns the introduced slurry or digestate.
- the precipitation container is provided for discharge with a tapered and funnel-shaped in flow cross-section tapered pipe section, and that the discharge itself with a
- Pipe connection flange is provided.
- Precipitation container is an upright, to be filled from bottom to top cylindrical container, and that the said turbulence by an eccentric to the vertical cylinder axis and placed on the bottom side
- Inlet opening for manure / digestate is generated.
- the said vortex is generated in the bottom region of the precipitation tank, which causes a good mixing of the incoming manure or digestate with the acidified water and the precipitant.
- Precipitant is arranged.
- Precipitant is arranged.
- a use according to the invention results from the fact that the said precipitation vessel is used in the operation of biogas plants operated with liquid manure in order to pretreat slurry streams prior to introduction into a respective fermenter of the said biogas plants, and subsequently with the resulting flocculation phase from the liquid manure to controlled feeding the fermenter performs.
- the biogas plant supplied slurry flows of Nutrient content through the said precipitation, but also a controlled desulfurization can be controlled / influenced to optimize the gas production.
- FIG. 2 Precipitation container in operative connection with FIG.
- Figure 5 precipitation container for the use of a
- FIG. 1 shows the precipitation container 1 according to the invention in various views.
- the upper row of figures shows the precipitation container in different
- the precipitation container is shown in plan view.
- the precipitation container consists of an upright cylindrical vessel 2, which is provided at the top with a connecting flange 8, on which an upper funnel-shaped conical projection 3 is formed, which then opens into a discharge opening 4 above.
- the manure / digestate is / are introduced from below, ie through the inlet opening 5, and at the same time, the injection of the precipitant through the injection port 6 takes place.
- the regulation of the precipitant feed can be made via a discharge area of the precipitated manure / digestate
- Introductory opening 7 is provided to supply, for example, water and / or anolyte, inter alia, as a separating agent.
- FIG. 2 shows schematically a representation in which the precipitation tank according to the invention below the manure / digestate is supplied together with the precipitant and / or with the acidified water.
- the chemically reacting mixture rises upwards, and is guided via the discharge opening, Figure 1 item number 4, in a knee-shaped tube, and from there up into the settling tank 10, which is provided with a sloping bottom. There it slips
- Foam / manure mixture then down and floats on a water level 11 presented water in
- the process is temporarily stopped, and the floating flake phase top stripped with a Skimmer 12 and brought out of the settling tank 10 out.
- the cloudy or clear phase, and if necessary, the deposited sedimentation are then present with clear phase separation, and said phases can then be withdrawn separately, and then the process continues with a new manure / fermentation residue - batch, etc.
- the Kayimmer 12 but also be placed below the settling tank, which is structurally compact and therefore advantageous, and the transfer pipe from the upper exit of the
- FIG. 3 shows the precipitation container again in a perspective view. It should be noted that the precipitation container is also upright in the operation of the invention, introduced the manure / digestate below and above after the reaction
- the precipitation vessel can also be used in the direct operation of biogas plants. This when using with manure
- Pre-treat fermenter of said biogas plants and thereafter performs a controlled feeding of the fermenter with the resulting flake phase from the manure.
- flows of the nutrient content can be controlled / influenced by said precipitation, but also a targeted desulfurization be made to optimize gas production.
- FIG. 4 shows a side view of a
- Precipitation container 1 with injection ports in the form of flanges at different heights.
- advantageous good mixing with precipitant is achieved in that one can adjust the injection height in the flow to the viscosity and consistency of the supplied streams by appropriate choice of one or more of the injection ports. It is important that the precipitant in the
- FIG. 5 shows an application example for the use, for example, of an H 2 S elimination by means of an iron chloride injection during the transfer of the liquid manure or digestate stream into a manure or fermentation residue store.
- the material flow is supplied via the flange near the bottom, the said injection is carried out via the injection ports with iron chloride and the material stream is discharged at the top.
- the discharge pipe is formed over elbows so that the Stoffström down below the precipitation tank, on the other side of the
- the advantage of such an arrangement is that the precipitation vessel can be built into the arrangement of pipelines at the same height therebetween.
Abstract
Description
Claims
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE102014011126 | 2014-07-28 | ||
DE102015001859.0A DE102015001859A1 (en) | 2014-07-28 | 2015-02-12 | Process and equipment for the treatment of agricultural manure and digestate |
PCT/EP2015/001490 WO2016015839A1 (en) | 2014-07-28 | 2015-07-20 | Method and device for treating liquid manure and fermentation remains |
Publications (1)
Publication Number | Publication Date |
---|---|
EP3174831A1 true EP3174831A1 (en) | 2017-06-07 |
Family
ID=55065552
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP15745148.5A Withdrawn EP3174831A1 (en) | 2014-07-28 | 2015-07-20 | Method and device for treating liquid manure and fermentation remains |
Country Status (3)
Country | Link |
---|---|
EP (1) | EP3174831A1 (en) |
DE (1) | DE102015001859A1 (en) |
WO (1) | WO2016015839A1 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116897672B (en) * | 2023-09-12 | 2023-12-15 | 田丰化工(山西)集团股份有限公司 | Novel water-soluble fertilizer applying device |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
ZA865990B (en) * | 1985-08-19 | 1987-03-25 | Peterson Filters Corp | Method and apparatus for use in separating solids from liquids |
US20080169245A1 (en) * | 2007-01-17 | 2008-07-17 | Soil Net Llc. | Solids separation technology |
CA2693117A1 (en) * | 2007-06-14 | 2008-12-24 | Kansas State University Research Foundation | Fluidized bed precipitator |
-
2015
- 2015-02-12 DE DE102015001859.0A patent/DE102015001859A1/en not_active Withdrawn
- 2015-07-20 EP EP15745148.5A patent/EP3174831A1/en not_active Withdrawn
- 2015-07-20 WO PCT/EP2015/001490 patent/WO2016015839A1/en active Application Filing
Non-Patent Citations (2)
Title |
---|
None * |
See also references of WO2016015839A1 * |
Also Published As
Publication number | Publication date |
---|---|
WO2016015839A1 (en) | 2016-02-04 |
DE102015001859A1 (en) | 2016-01-28 |
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