SE533563C2 - Procedure for extracting energy from organic waste - Google Patents

Procedure for extracting energy from organic waste

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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
Application number
SE0900306A
Other languages
Swedish (sv)
Other versions
SE0900306A1 (en
Inventor
Arne Lindahl
Original Assignee
Arne Lindahl
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 Arne Lindahl filed Critical Arne Lindahl
Priority to SE0900306A priority Critical patent/SE533563C2/en
Priority to PCT/SE2010/000029 priority patent/WO2010104440A1/en
Publication of SE0900306A1 publication Critical patent/SE0900306A1/en
Publication of SE533563C2 publication Critical patent/SE533563C2/en

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/04Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment drying
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/001Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for sludges or waste products from water treatment installations
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • C02F11/04Anaerobic treatment; Production of methane by such processes
    • 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
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • F23G5/46Recuperation of heat
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J1/00Removing ash, clinker, or slag from combustion chambers
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/20Dewatering by mechanical means
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/70Blending
    • F23G2201/701Blending with additives
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2206/00Waste heat recuperation
    • F23G2206/20Waste heat recuperation using the heat in association with another installation
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J2900/00Special arrangements for conducting or purifying combustion fumes; Treatment of fumes or ashes
    • F23J2900/01001Sorting and classifying ashes or fly-ashes from the combustion chamber before further treatment
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • 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
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater 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)

1. 533 563 PATENTKRAV Förfarande som innefattar utvinning av energi i olika former från suspensioner (1) med innehåll av organisk substans kännetecknat av att det organiska materialet behandlas i en kombination av integrerade steg varvid som första steg, utvinns biogas (3) medelst rötning av det organiska materialet varefter den efter rötning erhållen rötrest (4) i ett andra steg fórtjockas till torrhalter inom intervallet 5-25 % varefter den partiellt fórtjockade rötresten i ett tredje steg (6) blandas med avvattningsbefrärnjande medel (8) före ett fjärde steg som innefattar mekanisk avvattning (7) till en torrhalt av minst 48 % varvid utpressad vätska (14) förs till rötningskammaren (2) fore ett femte steg i form av termisk behandling under samtidig destruktion av kemikalier. F örfarande enligt krav l kännetecknat av att som avvattningsbefrämjande medel (8) används modifierat sågspån, Förfarande enligt krav 1 och 2 kännetecknat av att den termiska behandlingen innefattar förgasning av det koncentrerade organiska materialet (9). F örfarande enligt krav 1-3 kännetecknat av att den genererade gasen används för generering av värme och/eller elektricitet.. Förfarande enligt krav 1-3 kännctecknat av att den genererade biogasen används for att konverteras till organiska föreningar. Förfarande enligt krav l och 2 kännetecknat av att den termiska behandlingen innefattar förbränning (10) av det koncentrerade organiska materialet. F örfarande enligt krav 6 kännetecknat av att den vid förbränningen genererade energin konverteras till värme och/eller elektricitet (1 2,13). Förfarande enligt krav 6 kännetecknat av att den efter förbrärming erhållna askan (1 1) med innehåll av fosfor konverteras till granuler.A process comprising recovering energy in various forms from suspensions (1) containing organic matter, characterized in that the organic material is treated in a combination of integrated steps, in which, as a first step, biogas (3) is recovered by digestion of the organic material after which the digestate (4) obtained after digestion in a second step is thickened to dry matter contents in the range 5-25% after which the partially thickened digestate in a third step (6) is mixed with dewatering agent (8) before a fourth step comprising mechanical dewatering (7) to a dry matter content of at least 48%, whereby squeezed liquid (14) is fed to the digestion chamber (2) before a fifth step in the form of thermal treatment during simultaneous destruction of chemicals. Process according to Claim 1, characterized in that modified sawdust is used as the dewatering-promoting agent (8). Process according to Claims 1 and 2, characterized in that the thermal treatment comprises gasification of the concentrated organic material (9). Process according to claims 1-3, characterized in that the generated gas is used for generating heat and / or electricity. Process according to claims 1-3, characterized in that the generated biogas is used to be converted into organic compounds. Process according to claims 1 and 2, characterized in that the thermal treatment comprises combustion (10) of the concentrated organic material. Process according to Claim 6, characterized in that the energy generated during combustion is converted into heat and / or electricity (1, 2.13). Process according to Claim 6, characterized in that the ash (1 L) obtained after incineration is converted into granules.
SE0900306A 2009-03-10 2009-03-10 Procedure for extracting energy from organic waste SE533563C2 (en)

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

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SE (1) SE533563C2 (en)
WO (1) WO2010104440A1 (en)

Family Cites Families (5)

* Cited by examiner, † Cited by third party
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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Publication number Publication date
WO2010104440A1 (en) 2010-09-16
SE0900306A1 (en) 2010-09-11

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