SE533563C2 - Procedure for extracting energy from organic waste - Google Patents
Procedure for extracting energy from organic wasteInfo
- Publication number
- SE533563C2 SE533563C2 SE0900306A SE0900306A SE533563C2 SE 533563 C2 SE533563 C2 SE 533563C2 SE 0900306 A SE0900306 A SE 0900306A SE 0900306 A SE0900306 A SE 0900306A SE 533563 C2 SE533563 C2 SE 533563C2
- Authority
- SE
- Sweden
- Prior art keywords
- process according
- digestate
- organic material
- dewatering
- biogas
- Prior art date
Links
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/04—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment drying
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/001—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for sludges or waste products from water treatment installations
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- 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
- C02F11/02—Biological treatment
- C02F11/04—Anaerobic treatment; Production of methane by such processes
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
- F23G5/46—Recuperation of heat
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J1/00—Removing ash, clinker, or slag from combustion chambers
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/20—Dewatering by mechanical means
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/70—Blending
- F23G2201/701—Blending with additives
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2206/00—Waste heat recuperation
- F23G2206/20—Waste heat recuperation using the heat in association with another installation
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2900/00—Special arrangements for conducting or purifying combustion fumes; Treatment of fumes or ashes
- F23J2900/01001—Sorting and classifying ashes or fly-ashes from the combustion chamber before further treatment
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- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- 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
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- Water Supply & Treatment (AREA)
- General Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Hydrology & Water Resources (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
Description
533 563 Nackdelar med känd teknik Emedan det i samhället används kemikalier och att det sprids bakterier, virus och parasiter av olika slag återfinns många av dem i kommunala bioslam. Nämnas kan, att inom EU finns ca 110.000 kommersiella kemikalier registrerade. National Research Council, USA, har klassificerat 10 milj. kemikalier. Många av kemikaliema är hälsofarliga och därför bör rester av kommunala slam inte läggas ut på markytor. Dessutom har det visat sig, att vid spridning på åkrar sprids en odör som stör omgivningen. 533 563 Disadvantages of known technology Because chemicals are used in society and the spread of bacteria, viruses and parasites of various kinds, many of them are found in municipal biosludge. It can be mentioned that within the EU there are about 110,000 commercial chemicals registered. The National Research Council, USA, has classified 10 million. chemicals. Many of the chemicals are hazardous to health and therefore residues of municipal sludge should not be laid on land surfaces. In addition, it has been shown that when spreading in fields, an odor spreads which disturbs the surroundings.
Vid utvinning av biogas erhålls ett energiutbyte som ligger vid endast ca 1 MWh per ton organisk substans. Man har provat förbränning av rötrester (bioslam) men beroende på den höga halten av vatten har det inte varit möjligt att få ekonomi vid förbränningen. Vid förfarandet som beskrivs i patentet SE 523 787 är det dock möjligt att avvattna till torrhalter över 50 %.When extracting biogas, an energy yield of only about 1 MWh per tonne of organic matter is obtained. Incineration of digestate (biosludge) has been tried, but due to the high content of water, it has not been possible to obtain economics during incineration. However, in the process described in patent SE 523 787, it is possible to dewater to dry contents above 50%.
Beskrivning av uppfinningen Uppfinningen innefattar vitala processteg såsom fortjockning, framställning av metangas, avvattning, förbränning och/eller fórgasning. Apparater och deras funktion skall i det följande beskrivas med stöd av figur 1.Description of the invention The invention comprises vital process steps such as thickening, production of methane gas, dewatering, combustion and / or gasification. Apparatus and their function will be described in the following with reference to Figure 1.
Avlopp 1 från djurstallar, reningsverk eller en WC-stol förs till en rötningskammare 2 vari bildas biogas 3 i form av metan. Som restprodukt erhålls en rötrest, s k bioslam 4. Den efter framställning av biogasen erhållna rötresten är löst i stora volymer vatten. Emedan det i enlighet med uppfinningen ingår att förbränna rötresten måste avdrivas vatten. Detta sker genom att mekaniskt filtrera och/eller avvattna i ett eller flera steg. Vid föredragen forrn av uppfinningen förtjockas suspensionen till en torrhalt från cirka 5 % till cirka 25 % med hjälp av ett trumfilter 5 eller centrifug .Drainage 1 from animal stables, treatment plants or a toilet seat is taken to a digestion chamber 2 in which biogas 3 is formed in the form of methane. A digestate is obtained as a residual product, so-called biosludge 4. The digestate obtained after production of the biogas is dissolved in large volumes of water. Since it is included in accordance with the invention to burn the digestate, water must be evaporated. This is done by mechanically filtering and / or dewatering in one or more steps. In preferred embodiments of the invention, the suspension is thickened to a dry matter content of from about 5% to about 25% by means of a drum filter or centrifuge.
Enkännetecknande del av uppfinningen år att den partiellt förtjockade rötresten 6 förs till en press 7 eller dubbelviramaskin fiår ytterligare avdrivning av vatten så att torrhalten överstiger 48 %. 1 enlighet med patentskriften SE 523 787 kan före avvattningen rötresten blandas med avvattningsbefrämjande material i partikelform, som exempelvis modifierat sågspån. Detta altemativ är markerat med en streckad pil 8-i tig. 1. Ett annat sätt som kan tillämpas är att i enlighet med patentskriften SE 528 781 frysa ner rötresten och efter upptining utföra avvattningen. 533 563 3 Avvattnat slam 9 med en torrhalt över 48 % förs vidare till en iörbränningskarnmare 10 vars storlek varierar efter behov. , Vid förbränning av enbart rötresten krävs givetvis en mindre förbränningsugn än vid förbränning av rötresten i blandning med andra material. Företrädesvis ska det andra materialet bestå av så kallat biobränsle, som exempelvis ved, bark och bioolja.A characteristic part of the invention is that the partially thickened digestate 6 is fed to a press 7 or double wire machine fi further evaporation of water so that the dry matter content exceeds 48%. In accordance with patent specification SE 523 787, before dewatering, the digestate can be mixed with dewatering-promoting material in particulate form, such as modified sawdust. This alternative is marked with a dashed arrow 8-i tig. Another way that can be applied is to freeze the digestate in accordance with patent specification SE 528 781 and carry out the dewatering after thawing. 533 563 3 Dewatered sludge 9 with a dry content of more than 48% is passed on to an incinerator 10 whose size varies as required. When burning only the digestate, of course, a smaller incinerator is required than when burning the digestion in a mixture with other materials. Preferably, the second material should consist of so-called biofuel, such as wood, bark and bio-oil.
Vid förbränningen erhålls destruktion av syntetiska kemikalier. Som restprodukt erhålls aska 11 som innehåller oxider av bland armat kalcium, kalium och fosfor. Inom ramen för uppfinningen framställs granuler eller pellets av askan.During combustion, destruction of synthetic chemicals is obtained. As a residual product, ash 11 is obtained, which contains oxides of, among others, calcium, potassium and phosphorus. Within the scope of the invention, granules or pellets are produced from the ash.
Den vid förbränningen alstrad energi nyttjas som värme 12 och/eller för generering av elektricitet 13.The energy generated during combustion is used as heat 12 and / or to generate electricity 13.
Som altemativ till förbränning kan nyttjas förgasning, som konverterar koltöreningar till kolmonoxid och vätgas. Två energirika gaser vilka genom syntes kan bilda nya högvärdiga produkter, som t. ex. syntetisk disel.As an alternative to combustion, gasification can be used, which converts carbon compounds to carbon monoxide and hydrogen gas. Two energy-rich gases which through synthesis can form new high-quality products, such as synthetic diesel.
Utföringsexempel l reningsverket Knorthem hanteras årligen ca 300 ton torrt slam vilket blir ca 7500 ton/ms vid en torrhalt av 4 %. Efter generering av biogas iörtjockas rötresten (4) i en dekantercentrifug (5) till en torrhalt av 23 % i 2 % (faktiska).Execution example in the treatment plant Knorthem, approximately 300 tonnes of dry sludge is handled annually, which is approximately 7500 tonnes / ms at a dry matter content of 4%. After biogas generation, the digestate (4) in a decanter centrifuge (5) is thickened to a dry matter content of 23% in 2% (actual).
Eftersom innehållet av vatten i bioslammet (6) fortfarande var för stort för att förbrännas pressades rötslammet i en press (7) med två kolvar med genomgående ledningar för bortförsel av vätska, som medelst ledningen 14 återfördes till rötningskammaren (2). Recirkulationen innebär att ytterligare biogas kunde alstras då rötningsprocessen sällan är fullständig.Since the content of water in the biosludge (6) was still too large to be incinerated, the digestate sludge was pressed in a press (7) with two pistons with continuous lines for removal of liquid, which was returned to the digestion chamber (2) by means of line 14. The recirculation means that additional biogas could be generated as the digestion process is seldom complete.
Före pressningen blandades rötresten med modifierat sågspån (8) så att blandningen innehöll 40 vikts-% spån. Efter pressningen var torrhalten 57 % medan blandningens torrhalt före pressningen var 32,8 %.Prior to pressing, the digestate was mixed with modified sawdust (8) so that the mixture contained 40% by weight of sawdust. After pressing, the dry content was 57% while the dry content of the mixture before pressing was 32.8%.
Det teoretiska energivärdet vid torrhalten 57 % ligger vid cirka 4 MWh per ton rötrest räknat på organisk substans. Det teoretiska bidraget från rötresten blev hela 2,4 MWh (0,6x4,9).The theoretical energy value at a dry matter content of 57% is approximately 4 MWh per tonne of digestate based on organic matter. The theoretical contribution from the digestate was as much as 2.4 MWh (0.6x4.9).
Enligt uppfinningen är det således möjligt att vid framställning av biogas utvinna cirka l MWh och vid förbränning cirka 2,4 MWh, d v s totalt 3,4 MWh. Den teoretiska återvinningsgraden ligger således vid cirka 70 %.According to the invention, it is thus possible to extract about 1 MWh in the production of biogas and in combustion about 2.4 MWh, i.e. a total of 3.4 MWh. The theoretical recovery rate is thus around 70%.
Vid eldning av blandningen i ÖviksEnergi AB's biobränslepanna i Bredbyn kunde konstateras, att tömningen av rötrest-och spånblandningen från containern och matningen till eldstaden fungerade kl anderfritt. 533 563 Förbränningen av blandningen fórlöpte normalt och särskilt överraskande var att beläggningar i pannrummet minskade och att askan blev lätthanterlig i form av fritt pulver. Enligt beräkningar erhölls ett normalt värmeutbyte vid förbränningen eller ca 4,4 MWh per ton organisk substans (rötrest + spån).When firing the mixture in ÖviksEnergi AB's biofuel boiler in Bredbyn, it could be stated that the emptying of the digestate and chip mixture from the container and the feed to the fireplace worked smoothly. 533 563 The combustion of the mixture proceeded normally and it was particularly surprising that coatings in the boiler room decreased and that the ash became easy to handle in the form of free powder. According to calculations, a normal heat exchange was obtained during combustion or about 4.4 MWh per tonne of organic matter (digestate + shavings).
Av askan tillverkades granuler i en roterande trumma. Erhållna granuler blev relativt jämnstora (3-8 mm) och överraskande starka (hög densitet).Granules were made from the ash in a rotating drum. The granules obtained were relatively evenly sized (3-8 mm) and surprisingly strong (high density).
Askan innehöll överraskande hög halt, 6,5 %, av P2O5 (fosforpentaoxid), 6,2 % CaO (bränd kalk) och 3,5 % KzO (kaliumoxid). Askans ekonomiska värde kunde taxeras till minst 600 kr/ton. Några rester av organisk substans kunde inte återfinnas i askan, vilket visade att förbränningen hade dcstruerat syntetiska substanser. Beroende på att askan är alkalisk kunde ej heller återfinnas virus, bakterier eller parasiter i restprodukten aska.The ash contained a surprisingly high content, 6.5%, of P2O5 (phosphorus pentaoxide), 6.2% CaO (quicklime) and 3.5% K2O (potassium oxide). The economic value of the ash could be taxed at at least SEK 600 / tonne. No residues of organic matter could be found in the ash, which showed that the combustion had destroyed synthetic substances. Due to the fact that the ash is alkaline, no viruses, bacteria or parasites could be found in the residual product ash.
Fördelar med uppfinningen Uppfinningen har stor betydelse i strävan att skapa en bättre miljö i ett resurssnålare samhälle.Advantages of the invention The invention is of great importance in the effort to create a better environment in a more resource-efficient society.
Efter iörtjockning av rötresten, som erhålls efter framställning av biogas, erhålls ett material som vid förbränning kan generera energi. Sålunda kan från restprodukten rötrest (bioslam) genom alstring av biogas och förbränning altemativt fórgasning av rötrester utvinnas en ansenlig mängd energi. Genom återfóring av utpressad vätska till rötkarrimaren erhålls något högre utbyte av biogas.After thickening of the digestate, which is obtained after the production of biogas, a material is obtained which, when burned, can generate energy. Thus, a considerable amount of energy can be extracted from the residual product, digestate (biosludge) by generating biogas and combustion or alternatively pre-gasifying of digestate. By returning extruded liquid to the digester, a slightly higher yield of biogas is obtained.
Särskilt värdefullt är att ur folkhälsosynpunkt erhålls en effektiv destruktion av potentiellt farliga kemikalier, virus, bakterier och parasiter..Particularly valuable is that from a public health point of view, an efficient destruction of potentially dangerous chemicals, viruses, bacteria and parasites is obtained.
En annan fördel med förfarandet enligt uppfinningen är att det en erhålls en värdefull restprodukt i fonn av högvärdi g aska med innehåll av värdefulla kemikalier, vilka kan nyttjas för odlingAnother advantage of the process according to the invention is that a valuable residual product is obtained in the form of high-value gas containing valuable chemicals, which can be used for cultivation.
Claims (1)
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
SE0900306A SE533563C2 (en) | 2009-03-10 | 2009-03-10 | Procedure for extracting energy from organic waste |
PCT/SE2010/000029 WO2010104440A1 (en) | 2009-03-10 | 2010-02-08 | Recovery of energy from organic wastes |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
SE0900306A SE533563C2 (en) | 2009-03-10 | 2009-03-10 | Procedure for extracting energy from organic waste |
Publications (2)
Publication Number | Publication Date |
---|---|
SE0900306A1 SE0900306A1 (en) | 2010-09-11 |
SE533563C2 true SE533563C2 (en) | 2010-10-26 |
Family
ID=42728555
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
SE0900306A SE533563C2 (en) | 2009-03-10 | 2009-03-10 | Procedure for extracting energy from organic waste |
Country Status (2)
Country | Link |
---|---|
SE (1) | SE533563C2 (en) |
WO (1) | WO2010104440A1 (en) |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CA1070864A (en) * | 1977-06-10 | 1980-01-29 | Komline-Sanderson Engineering Corporation | Sludge dewatering process |
FR2758100B1 (en) * | 1997-01-06 | 1999-02-12 | Youssef Bouchalat | OPTIMIZED PROCESSING AND ENERGY RECOVERY OF SLUDGE FROM URBAN AND INDUSTRIAL PURIFICATION PLANTS |
US6410283B1 (en) * | 2001-06-07 | 2002-06-25 | Endesco Clean Harbors, L.L.C. | Conversion of sewage sludge into electric power |
SE523787C2 (en) * | 2002-01-23 | 2004-05-18 | Arne Lindahl | Process for draining liquid from difficult dewatered materials |
SE528781C2 (en) * | 2002-12-04 | 2007-02-13 | Lindahl Arne | Dewatering method, e.g. for sludge, involves converting material into granules or pellets and then cooling before dewatering |
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2009
- 2009-03-10 SE SE0900306A patent/SE533563C2/en unknown
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2010
- 2010-02-08 WO PCT/SE2010/000029 patent/WO2010104440A1/en active Application Filing
Also Published As
Publication number | Publication date |
---|---|
WO2010104440A1 (en) | 2010-09-16 |
SE0900306A1 (en) | 2010-09-11 |
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