SE533702C2 - Treatment of sewage - Google Patents
Treatment of sewageInfo
- Publication number
- SE533702C2 SE533702C2 SE0800652A SE0800652A SE533702C2 SE 533702 C2 SE533702 C2 SE 533702C2 SE 0800652 A SE0800652 A SE 0800652A SE 0800652 A SE0800652 A SE 0800652A SE 533702 C2 SE533702 C2 SE 533702C2
- Authority
- SE
- Sweden
- Prior art keywords
- liquid
- carburettor
- water
- ammonia
- thickener
- Prior art date
Links
- 239000010865 sewage Substances 0.000 title claims 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 34
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 16
- 229910021529 ammonia Inorganic materials 0.000 claims description 15
- 239000007788 liquid Substances 0.000 claims description 14
- 239000007789 gas Substances 0.000 claims description 9
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 claims description 6
- 238000006243 chemical reaction Methods 0.000 claims description 6
- 239000003415 peat Substances 0.000 claims description 6
- 229910052782 aluminium Inorganic materials 0.000 claims description 4
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 4
- 239000000126 substance Substances 0.000 claims description 4
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 2
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 2
- 239000004571 lime Substances 0.000 claims description 2
- 229910001629 magnesium chloride Inorganic materials 0.000 claims description 2
- 239000004576 sand Substances 0.000 claims description 2
- 238000000034 method Methods 0.000 claims 4
- 230000005494 condensation Effects 0.000 claims 1
- 238000009833 condensation Methods 0.000 claims 1
- 230000000087 stabilizing effect Effects 0.000 claims 1
- 239000002562 thickening agent Substances 0.000 description 17
- 150000003839 salts Chemical class 0.000 description 8
- 229910052751 metal Inorganic materials 0.000 description 6
- 239000002184 metal Substances 0.000 description 6
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 6
- 239000000203 mixture Substances 0.000 description 5
- 239000002023 wood Substances 0.000 description 5
- PAWQVTBBRAZDMG-UHFFFAOYSA-N 2-(3-bromo-2-fluorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=CC(Br)=C1F PAWQVTBBRAZDMG-UHFFFAOYSA-N 0.000 description 4
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 4
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 4
- 239000003337 fertilizer Substances 0.000 description 4
- 239000008187 granular material Substances 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 239000002253 acid Substances 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 229920005610 lignin Polymers 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 2
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 238000000855 fermentation Methods 0.000 description 2
- 230000004151 fermentation Effects 0.000 description 2
- 239000000835 fiber Substances 0.000 description 2
- 238000002309 gasification Methods 0.000 description 2
- 239000005431 greenhouse gas Substances 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- -1 hydroxyethoxy ethyl Chemical group 0.000 description 2
- 239000006028 limestone Substances 0.000 description 2
- 239000011777 magnesium Substances 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000001856 Ethyl cellulose Substances 0.000 description 1
- 229920001732 Lignosulfonate Polymers 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical class [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 238000005903 acid hydrolysis reaction Methods 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 238000003287 bathing Methods 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 239000002551 biofuel Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 235000019504 cigarettes Nutrition 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000005202 decontamination Methods 0.000 description 1
- 230000003588 decontaminative effect Effects 0.000 description 1
- 238000004851 dishwashing Methods 0.000 description 1
- 229920001249 ethyl cellulose Polymers 0.000 description 1
- 235000019325 ethyl cellulose Nutrition 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000001764 infiltration Methods 0.000 description 1
- 230000008595 infiltration Effects 0.000 description 1
- 230000002045 lasting effect Effects 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 159000000003 magnesium salts Chemical class 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 235000019341 magnesium sulphate Nutrition 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 235000008935 nutritious Nutrition 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000008213 purified water Substances 0.000 description 1
- 239000008237 rinsing water Substances 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 229910021653 sulphate ion Inorganic materials 0.000 description 1
- 230000008719 thickening Effects 0.000 description 1
- 239000012808 vapor phase Substances 0.000 description 1
- 235000013311 vegetables Nutrition 0.000 description 1
- 229910052725 zinc Chemical class 0.000 description 1
- 239000011701 zinc Chemical class 0.000 description 1
Classifications
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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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
- C02F1/586—Treatment of water, waste water, or sewage by removing specified dissolved compounds by removing ammoniacal nitrogen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05C—NITROGENOUS FERTILISERS
- C05C1/00—Ammonium nitrate fertilisers
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F7/00—Fertilisers from waste water, sewage sludge, sea slime, ooze or similar masses
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/20—Treatment of water, waste water, or sewage by degassing, i.e. liberation of dissolved gases
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/286—Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- 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
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
- C02F11/04—Anaerobic treatment; Production of methane by such processes
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- 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
- C02F2103/002—Grey water, e.g. from clothes washers, showers or dishwashers
-
- 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
- C02F2103/005—Black water originating from toilets
-
- 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
- C02F2303/00—Specific treatment goals
- C02F2303/02—Odour removal or prevention of malodour
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/06—Aerobic processes using submerged filters
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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
- 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
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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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
- Treating Waste Gases (AREA)
Description
533 702 2/ förtjockaren. l sluttande terräng kan nyttjas självavrinning från förtjoekaren. Givetvis kan, oavsett terräng, användas pumpar. Förtjockarens dimensioner varieras efter behov. 533 702 2 / thickener. In sloping terrain, self-drainage from the thickener can be used. Of course, regardless of the terrain, pumps can be used. The dimensions of the thickener are varied as needed.
En förtjockare med exempelvis en diameter av 500 mm och en höjd av 800 mm har en kapacitet att förtjocka ca 300 liter per timme. Ett normalt hushåll förbrukar maximalt 200 liter vatten per dygn.A thickener with, for example, a diameter of 500 mm and a height of 800 mm has a capacity to thicken about 300 liters per hour. A normal household consumes a maximum of 200 liters of water per day.
För att underlätta tömningen, d v s att minska vikten via förtjockning och självtorkning är det givetvis fördelaktigt att växelvis använda två törtjockare. Detta medger längre tid för dränering och självtorkning. Vid temperaturer över nollstrecket kan dessutom erhållas en förmultning som ytterligare minskar den fasta delens vikt. Sådan förrnultning (anaerob) leder vanligtvis till bildning av metan (biogas), som har högt energivärde. Framställning av metan via anaerob rötning är framförallt av intresse vid stora anläggningar vilka betjänar minst tio WC-stolars avlopp. Bättre ekonomsikt utbyte erhålls om det förtjockade materialet förbränns eller nyttjas i en förgasningsanläggning. Vid stora anläggningar vilka betjänar minst fem hushåll används företrädesvis kontinuerligt arbetande förtjoekare i form av till exempel tmmfilter vilka kan kompletteras med skruv-eller kolvpress.To facilitate emptying, ie to reduce weight via thickening and self-drying, it is of course advantageous to use two dry thickeners alternately. This allows longer time for drainage and self-drying. In addition, at temperatures above the zero line, a decay can be obtained which further reduces the weight of the solid part. Such decontamination (anaerobic) usually leads to the formation of methane (biogas), which has a high energy value. Production of methane via anaerobic digestion is of particular interest in large plants which serve the drains of at least ten toilet seats. Better economic return is obtained if the thickened material is incinerated or used in a gasification plant. In large plants which serve at least five households, continuously operating thickeners are preferably used in the form of, for example, empty filters which can be supplemented with screw or piston presses.
Det förtjockade materialet kan givetvis även användas som gödningsmedel, som med fördel blandas med utvunnet ammoniumnitrat (vars framställning beskrivs senare). Det så utvunna naturgödslet ska givetvis användas på ytor som ligger på s a s säkert avstånd från vattendrag.The thickened material can of course also be used as a fertilizer, which is advantageously mixed with recovered ammonium nitrate (the preparation of which is described later). The natural manure thus extracted must of course be used on surfaces that are at a safe distance from watercourses.
Produkten bör inte heller användas för odling av grönsaker.The product should also not be used for growing vegetables.
För att få ett jämnt flöd.e till förtjockaren kan placeras någon typ av buffert (ej visad i tig.) mellan WC-stolen och förtjockaren. Sådan buffert kan bestå av ett kärl eller ett rör som krökts till att bilda skruvliknande (snäcka) konfiguration. l avsikt att förhindra lukt och samtidigt kunna effektivt tömma vätska från behållaren (hindra undertryck) förses förtjockarens övre del med ett permeabelt gasfilter 6. Sådant gasfilter kan framställas av torvfibrer och lignocellulosafibrer i blandning med lämpligt bindemedel som exempelvis lignosulfonat, cellulosaderivat (t.ex. hydroxietoxi etyl-cellulosa) samt restprodukter. Företrädesvis nyttjas restlignin efter sur hydrolys av ved, fiberslam och/eller bioslain. Gasfiltret bör ha en porös struktur, men samtidigt vara härdig mot väta. och ha en exponerad och aktiv yta av >10m2/g.To get an even till öd.e to the thickener, some type of buffer (not shown in fig.) Can be placed between the toilet seat and the thickener. Such a buffer may consist of a vessel or tube which is curved to form a screw-like (screw) configuration. In order to prevent odor and at the same time be able to effectively drain liquid from the container (prevent negative pressure), the upper part of the thickener is provided with a permeable gas filter 6. Such a gas filter can be made of peat fibers and lignocellulosic mixtures in mixture with suitable binder such as lignosulfonate, cellulose derivatives. hydroxyethoxy ethyl cellulose) and residues. Preferably, the residual lignin is used after acid hydrolysis of wood, sludge and / or bioslain. The gas filter should have a porous structure, but at the same time be resistant to moisture. and have an exposed and active surface area of> 10m2 / g.
En variant av gasfiltret är att använda aktivt kol. En annan variant är att fylla filtret med granuler vilka har olika egenskaper (som exempelvis storlek och densitet).A variant of the gas filter is to use activated carbon. Another variant is to fill the filter with granules which have different properties (such as size and density).
Ytterligare en variant utgör tillsats av malet vedmaterial såsom sågspån, flis och kvist. Vidare kan ingå li gnin, som erhålls som restprodukt vid framställning av etanol och sulfatmassa från ved. Huvudsaken är att gasfiltrets material tillåter varaktig och god luftgenoniströmniitg. 533 702 Från förtjockaren förs vätska via ledningen 5 till en förgasare 7 på vars botten ligger granuler 8 av kalk och/eller aska. Företrädesvis används aska, som erhålls efter förbränning av biobränslen. lnom ramen för uppfinningen kan mellan förtjockaren och förgasaren placeras en behållare som fungerar likt en buffert och medger en ytterligare behandling av vätskan.Another variant is the addition of ground wood material such as sawdust, wood chips and twigs. Furthermore, lignin obtained as a residual product in the production of ethanol and sulphate pulp from wood may be included. The main thing is that the material of the gas filter allows lasting and good air genome flow. 533 702 From the thickener, liquid is conveyed via the line 5 to a carburettor 7 on the bottom of which granules 8 of lime and / or ash lie. Preferably, ash is obtained, which is obtained after combustion of biofuels. Within the framework of the invention, a container can be placed between the thickener and the carburettor, which acts like a buffer and allows a further treatment of the liquid.
Beroende på reaktioner mellan vätskan och de alkaliska granulerna i förgasaren frigörs ammoniak, som bringas i kontakt med ett metall salt 9, som exempelvis magnesiumklorid (MgClz) och/eller magnesiumsulfat (MgSO4). Andra lämpliga katjoner är salter av aluminium och zink. Vidare kan med fördel användas lättmetaller och företrädesvis aluminium, som med ammoniak avger vätgas. För effektiv reaktion tillförs aluminiumet i partikelform. Innan gasen fås att reagera med saltet avlägsnas den vattenånga som kan finnas med ammoniaken. Enklast sker detta genom att kondensera gasblandningen i en kylare 10 varvid vattenångan överförs från ångfas tillvätskefas medan ammoniakgasen förs vidare för reaktion med metallsaltet..Depending on the reactions between the liquid and the alkaline granules in the carburettor, ammonia is released, which is brought into contact with a metal salt 9, such as magnesium chloride (MgCl 2) and / or magnesium sulphate (MgSO 4). Other suitable cations are salts of aluminum and zinc. Furthermore, light metals and preferably aluminum can be used to advantage, which emit hydrogen gas with ammonia. For efficient reaction, the aluminum is added in particulate form. Before the gas is reacted with the salt, the water vapor that may be present with the ammonia is removed. This is most easily done by condensing the gas mixture in a cooler 10, the water vapor being transferred from the vapor phase to the liquid phase while the ammonia gas is passed on for reaction with the metal salt.
Genom en kemisk reaktion mellan animoniaken och metallsaltet erhålls en metallamin, som till exempel Mg(N H3)6Cl2 (eller Mg(NH3)6SO4). En variant är att fånga upp ammoniak med en utspädd syra i ett ”jäsningsrör” ll. Företrädesvis används salpetersyra som med ammoniak bildar ammoniumnitrat i ”j äsníngsröret”. F örgasaren kan kompletteras med ett kärl 12, som förlänger tiden för ammoniakens avgång. Fri gjord ammoniak leds via ledningen 13 till kylaren (10) för att ledas vidare till metallsaltet (eller syran).A chemical reaction between the ammonia and the metal salt gives a metal amine, such as Mg (N H3) 6Cl2 (or Mg (NH3) 6SO4). One variant is to capture ammonia with a dilute acid in a "fermentation tube" ll. Preferably, nitric acid is used which, with ammonia, forms ammonium nitrate in the "fermentation tube". The carburettor can be supplemented with a vessel 12, which prolongs the time for the ammonia to escape. Released ammonia is passed via line 13 to the cooler (10) to be passed on to the metal salt (or acid).
Praktiskt taget kvävefri vätska förs från förgasaren (alternativt från kärlet 12) till ett kombifilter 14 vars första steg kan innefatta sand och ett andra steg med torv och eller bark. Även blandningar av bark och torv kan nyttjas. En kännetecknande del av uppfinningen är att medelst ledningen 15 återföra det genom filtret renade vattnet till WC-stolen. Det kan vara lämpligt, att före sådan recirkulation, rena vattnet i ett tämligen enkelt filter 16 som finns tillgänglig på marknaden. Det kan räcka med ett UV-”filter”. Efter sådan rening kan vattnet även användas till bad och dusch. Inom ramen för uppfinningen kan vattnet från kombifiltret föras direkt ut till mark 17 för infiltration. [nom ramen för uppfinningen kan även behandlas disk-och duschvatten- Lltföringsexempel enligt uppfinningen I en sommarstuga installerades en WC-stol vars avlopp fördes till en förtjockare. Som avskiljare användes en perforerad plastsäck placerad i en tunna med förslutningsring.Practically nitrogen-free liquid is passed from the carburettor (alternatively from the vessel 12) to a combi filter 14, the first stage of which may comprise sand and a second stage of peat and / or bark. Mixtures of bark and peat can also be used. A characteristic part of the invention is to return the water purified through the filter to the toilet seat by means of the line 15. It may be appropriate, before such recirculation, to purify the water in a fairly simple filter 16 available on the market. A UV "alter" may suffice. After such purification, the water can also be used for bathing and showering. Within the scope of the invention, the water from the combi filter can be carried directly out to ground 17 for infiltration. In accordance with the invention, dishwashing and shower water can also be treated. A perforated plastic bag placed in a barrel with a sealing ring was used as a separator.
På locket monterades ett gasfilter bestående av granuler (diameter 1-2 mm) tillverkade av torv, massafibrer (slipmassa) och restlignin erhållen från tillverkning av etanol från ved. 533 702 År Avskild vätska fördes till en förgasare fylld med kalksten vars dimensioner varierade från 2 mm upp till 10 mm. Vid kontakt mellan vätskan och kalkstenen erhölls bildning av ammoniak. Denna ammoniak fångades upp av ett saltlager av magnesiumklorid.A gas filter consisting of granules (diameter 1-2 mm) made of peat, pulp fibers (abrasive pulp) and residual lignin obtained from the production of ethanol from wood was mounted on the lid. 533 702 Year Separated liquid was taken to a carburettor filled with limestone whose dimensions varied from 2 mm up to 10 mm. Upon contact between the liquid and the limestone, the formation of ammonia was obtained. This ammonia was captured by a salt layer of magnesium chloride.
Den i princip kvävefria vätskan fördes till ett biofilter som bestod av torv och bark. Partiellt renat vatten samlades i en behållare med volymen l00 liter. Vid behov pumpades vatten från behållaren till stugans WC-stol.The basically nitrogen-free liquid was taken to a biolter consisting of peat and bark. Partially purified water was collected in a container with a volume of 100 liters. If necessary, water was pumped from the container to the cottage's toilet seat.
Beskrivet relativt enkla försök utfördes under en sommarmånad vid användning av en första törtjockare. Anläggningen fortsattes att nyttjas resten av sommaren genom att investera i en andra törtjockare. Under hela perioden uppträdde inga stömingar med avseende på lukt eller vätskeflöden.Described relatively simple experiments were performed during a summer month using a first dry thickener. The plant continued to be used for the rest of the summer by investing in a second thickener. Throughout the period, no disturbances occurred with respect to odor or liquid fl fate.
Vid testen användes WC-stolen ca fem gånger per dygn. Emedan försöket pågick under 30 dagar och volymen spolvatten uppgick till 12 liter per gång blev den totala volymen till första förtjockaren ca 1800 liter medan volymen i avskiljaren vid försökets avbrott var endast 17 liter. När testen avbröts uttogs prov för mätning av torrhalten. Därvid visade det sig att torrhalten var 14 %, Den fasta substansen var med andra ord endast 2,4 kg ( l7x0. 14). Redan efter ett dygn var torrhalten så hög som 32 %. Således ett mycket överraskande resultat. Efter två veckor var torrhalten så hög som Sl % och totala vikten (substans +vatten) endast 4.6 kg.During the test, the toilet seat was used about five times a day. While the experiment lasted for 30 days and the volume of rinsing water amounted to 12 liters at a time, the total volume of the first thickener was about 1800 liters, while the volume in the separator at the interruption of the experiment was only 17 liters. When the test was interrupted, samples were taken to measure the dry content. The dry matter was found to be 14%. In other words, the solids content was only 2.4 kg (17x0.14). Even after 24 hours, the dry matter content was as high as 32%. Thus a very surprising result. After two weeks, the dry matter content was as high as Sl% and the total weight (substance + water) was only 4.6 kg.
Vad beträffar upptagning av ammoniak i magnesiumsaltet fungerade detta väl och vid upphettning kunde frigöras vätgas som antändes med cigarettändare. I brist på laboratorieutrustnin g fanns inte möjlighet att kvantifiera volymen vätgas..As for the uptake of ammonia in the magnesium salt, this worked well and upon heating, hydrogen gas could be released which was ignited with cigarette lighters. Due to a lack of laboratory equipment, it was not possible to quantify the volume of hydrogen.
Fördelar .Vid tillämpning av uppfinningen erhålls flera fördelar. Sålunda minskar utsläppet av bland annat växthusgasen ammoniak genom reaktion med salter eller en syra. Erhållna blandningar vari ammoniak ingår kan generera vätgas eller användas som gödningsmedel (t ex amnioniumnitrat). som kan ersätta en del av handelgödseln. som slukar energi vid tillverkningen.. Därför bidrar konceptet i enlighet med uppfinningen till att även indirekt minska utsläppet av en annan växthusgas, nämligen koldioxid. Ammoniumnitratet kan blandas med den törtj ockade resten som erhålls i förtjockaren. Således erhålls en näringsrik och ”ekologisk” gödsel. I stora anläggningar kan innehållet i förtjockaren nyttjas för rötning och bildning av metan, Andra altemativ är íörgasning som ger högt energiutbyte.Advantages When applying the invention, your advantages are obtained. Thus, the emission of, among other things, the greenhouse gas ammonia is reduced by reaction with salts or an acid. Mixtures obtained containing ammonia can generate hydrogen or be used as a fertilizer (eg ammonium nitrate). which can replace part of the commercial fertilizer. which consumes energy during production. Therefore, the concept in accordance with the invention contributes to also indirectly reducing the emission of another greenhouse gas, namely carbon dioxide. The ammonium nitrate can be mixed with the thickened residue obtained in the thickener. Thus, a nutritious and "organic" fertilizer is obtained. In large plants, the contents of the thickener can be used for digestion and formation of methane. Other alternatives are gasification, which provides a high energy yield.
Förtjockarens innehåll kan även iörbrännas. .The contents of the thickener can also be burned. .
Llppfinningen resulterar i minskad vattentörbrukning. lnte minst viktigt är att systemet kan användas inom områden där bristen på vatten är ett stort problem.Running results in reduced water consumption. Not least, the system can be used in areas where water shortages are a major problem.
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SE0800652A SE533702C2 (en) | 2008-03-20 | 2008-03-20 | Treatment of sewage |
PCT/SE2009/000139 WO2009116921A1 (en) | 2008-03-20 | 2009-03-17 | A method for removal of ammonia from waste from stables and water closets |
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DE50005812D1 (en) * | 1999-09-13 | 2004-04-29 | Joerg Oldenburg | USE OF A FILTER IN A FILTER SYSTEM FOR ODOR, DUST AND BODY EXHAUST |
JP2002079299A (en) * | 1999-10-19 | 2002-03-19 | Mitsubishi Heavy Ind Ltd | Method for treating ammonia-containing waste |
US6866779B1 (en) * | 2002-07-22 | 2005-03-15 | Western Environmental Engineering Company | Nitrogen recovery system and method |
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