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JPH04507217A - Methods and apparatus for treating materials from which methane and other chemicals harmful to the environment are released - Google Patents

Methods and apparatus for treating materials from which methane and other chemicals harmful to the environment are released

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Publication number
JPH04507217A
JPH04507217A JP2511502A JP51150290A JPH04507217A JP H04507217 A JPH04507217 A JP H04507217A JP 2511502 A JP2511502 A JP 2511502A JP 51150290 A JP51150290 A JP 51150290A JP H04507217 A JPH04507217 A JP H04507217A
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Prior art keywords
gas
combustion
cleaning
methane
starting material
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Japanese (ja)
Inventor
テルロウ,アリー
コッデ,ヤン
グラベランド,アントニー
Original Assignee
エネルギーベスパレンデ ミリオイ テクニーク ベスローテン フェンノートシャップ
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Publication of JPH04507217A publication Critical patent/JPH04507217A/en
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    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F3/00Fertilisers from human or animal excrements, e.g. manure
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05BPHOSPHATIC FERTILISERS
    • C05B17/00Other phosphatic fertilisers, e.g. soft rock phosphates, bone meal
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/20Capture or disposal of greenhouse gases of methane
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/145Feedstock the feedstock being materials of biological origin
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Fertilizers (AREA)
  • Treatment Of Sludge (AREA)
  • Treating Waste Gases (AREA)
  • Incineration Of Waste (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるため要約のデータは記録されません。 (57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 メタン及び環境に有害な他の m 放出される を 理 る 2 び 室 環境汚染によって惹き起こされる問題に関連して、環境に有害な化学物質を廃棄 物から除去することは極めて重要なことである。[Detailed description of the invention] Methane and other substances harmful to the environment 2 chambers that control the release Disposal of environmentally harmful chemicals related to problems caused by environmental pollution It is extremely important to remove it from objects.

乳牛、子牛、豚の肥料を輸送や保存したり地上に撒いた場合、及び排水汚泥のよ うな汚泥の輸送、保存、及び処理中に、かなりの量のメタン、アンモニア及び硫 化水素が放出される。特にアンモニア及び硫化水素は環境に非常に有害である。When manure from dairy cows, calves, and pigs is transported, stored, or spread on the ground, and when wastewater sludge is Significant amounts of methane, ammonia and sulfur are produced during transport, storage and processing of sludge. Hydrogen chloride is released. Ammonia and hydrogen sulfide in particular are very harmful to the environment.

アンモニアは化学的及び生物学的に酸化されて亜硝酸及び硝酸になり、それらは 酸性雨を生ずる。Ammonia is chemically and biologically oxidized to nitrite and nitric acid, which are Causes acid rain.

硫化水素は腐った卵のような悪臭のするガスであり、高濃度では非常に毒性の高 いものになる。この物質は酸化されて亜硫酸及び硫酸になり、それらも酸性雨の 成分になる。Hydrogen sulfide is a gas that smells like rotten eggs and is highly toxic at high concentrations. Become something. This substance is oxidized to sulfurous acid and sulfuric acid, which are also produced by acid rain. Becomes an ingredient.

メタンもオゾン層に害を与えるであろう。Methane will also harm the ozone layer.

従って、農場で大気中に流れ出るこれらの環境に有害めて重要なことである。Therefore, these environmentally hazardous emissions that are released into the atmosphere on farms are of great importance.

広義には、本発明は、メタン及び環境に有害な他の化学物質が放出される夫々の 材料を処理する方法に関し、この場合、この材料を加熱し、放出されるガスを水 又は化学的ガス洗浄循環溶液で洗浄処理にかけ、洗浄装置から放出されるガス中 のメタンを燃焼し、発生する熱を少なくとも部分的に出発材料を加熱するのに用 いる。Broadly speaking, the present invention applies to each Regarding the method of processing the material, in this case the material is heated and the gas released is immersed in water. or subjected to a cleaning process with a chemical gas cleaning circulation solution and in the gases released from the cleaning equipment. of methane and the heat generated is used at least partially to heat the starting material. There is.

燃焼中に発生した過剰の熱を、異なった加熱目的、例えば集中暖房に用いてもよ い。The excess heat generated during combustion may be used for different heating purposes, for example for central heating. stomach.

本発明の方法は、肥料及び(又は)排泄物を処理するのに用いても成功を収める ことができる。農場でこの方法を用いる場合、もし望むならば、家畜が住んでい る厩舎からの舎内空気を収り出すのと同時に、その舎内空気を向流状に同じ洗浄 装置又は別の洗浄装置で洗浄することを行なってもよい。出来るだけ良好な精製 を行わせるため、出来るだけ冷たい水、例えば12℃より低い水を洗浄に用いる のが好ましい。このような条件により、出来るだけ多くのアンモニア及び硫化水 素を向流状に洗浄されたガスから除去することができる。なぜなら、水の温度が 低いことにより、ガス流中の水蒸気の大部分が凝縮る。洗浄水として地下水中に 入れたタンクからの水を、その水は通常温度が低い(10℃)ので、用いること ができる。勿論、タンクも水道水で冷却することができる。The method of the invention can also be successfully used to treat manure and/or excreta. be able to. When using this method on the farm, if desired, At the same time as the indoor air from the stable is removed, the indoor air is also washed in a countercurrent manner. Cleaning may be carried out in the device or in a separate cleaning device. Purification as good as possible Use as cold water as possible, for example, water below 12°C, for washing. is preferable. Under these conditions, as much ammonia and sulfide water as possible can be removed. Elements can be removed from the scrubbed gas countercurrently. Because the water temperature The low temperature causes most of the water vapor in the gas stream to condense. into groundwater as cleaning water Use water from the tank you put it in, as that water is usually at a low temperature (10°C). Can be done. Of course, the tank can also be cooled with tap water.

洗浄装置では、上方へ流れるガスと、下方へ流れる水との接触を出来るだけ向上 させるため、サドル型装置のような慣用的充填床装置を適用するのが好ましい。In the cleaning equipment, the contact between the gas flowing upward and the water flowing downward is improved as much as possible. For this purpose, it is preferred to apply conventional packed bed equipment, such as saddle type equipment.

更に、上方へ粒径が減少して行く充填装置が配備された凝縮塔を通ってガスを上 方へ、その上に噴霧される水とは自流状に誘導するのが好ましい。Furthermore, the gas is passed through a condensation column equipped with a packing device whose particle size decreases upward. It is preferable that the water sprayed thereon be guided in a self-current manner.

凝縮塔の底に集められたアンモニア溶液も硫化水素を含み、それはガス流から洗 浄除去され、その硫化水素は水酸化鉄スラッジにその溶液を通すことにより硫化 鉄に転化させてもよい。形成された硫化鉄は、それから鉄を回収するため溶鉱炉 関係へ販売することができる。もし望むならば、アンモニアを水酸化アンモニウ ム溶液としてスラッジ層の上の水中に収集してもよい。凝縮装置中その溶液を循 環洗浄液体として用いる場合、その溶液のアンモニア含有量は50%にさえ上昇 してもよい。その後でタンク中の溶液を奇麗な水によって置き換えてもよい。The ammonia solution collected at the bottom of the condensation column also contains hydrogen sulfide, which is washed from the gas stream. The hydrogen sulfide is sulfurized by passing the solution through iron hydroxide sludge. May be converted to iron. The formed iron sulfide is then sent to a blast furnace to recover the iron. Can be sold to relationships. If desired, replace the ammonia with ammonium hydroxide. It may be collected in water above the sludge layer as a sludge solution. Circulating the solution through the condenser When used as a ring cleaning liquid, the ammonia content of the solution increases to even 50% You may. The solution in the tank may then be replaced with clean water.

勿論本発明による方法は、サイロに貯蔵された肥料にも適用することができる。Of course, the method according to the invention can also be applied to fertilizers stored in silos.

農場でこのように処理された肥料は殆どアンモニア及び硫化水素を含まないので 、後で通常のやり方で地面に撒いても、そうすることによって環境に有害な多量 の化学物質が大気中に流れることはない。Fertilizers treated in this way on farms contain almost no ammonia and hydrogen sulfide. , even if later spread on the ground in the usual way, doing so will result in large amounts that are harmful to the environment. of chemicals are not released into the atmosphere.

多量の余分な肥料が存在する場合、本発明の方法により加熱され濃縮されたその 余分な肥料は燃焼炉で燃焼することができる。その場合、NH,及びH,Sが除 去されたメタンガスも同じ炉で燃焼することができる。その場合、環境に有害な 硫黄酸化物及び窒素酸化物が形成される。そのことが、燃焼炉からきたそれらガ スを熱交換器を経て酸化カルシウム床に通過させる理由である。燃焼ガス中の硫 黄酸化物及び窒素酸化物と反応するCaOは、硫酸カルシウム及び硝酸カルシウ ムに転化する。更に、燐酸塩を含む鉱物残渣は燃焼空間の底に収集される。この 残渣は、硫黄及び窒素の酸化物をCaOに結合させることにより形成された燐酸 カルシウム及び硝酸カルシウムと混合することにより、カルシウム、窒素及び燐 酸塩を含む価値のある肥料を与える。If a large amount of excess fertilizer is present, it can be heated and concentrated according to the method of the invention. Excess fertilizer can be burned in a combustion furnace. In that case, NH, H, and S are excluded. The removed methane gas can also be combusted in the same furnace. In that case, environmentally harmful Sulfur oxides and nitrogen oxides are formed. This means that those gases coming from the combustion furnace This is why the gas is passed through a heat exchanger and into a bed of calcium oxide. Sulfur in combustion gas CaO, which reacts with yellow oxides and nitrogen oxides, is calcium sulfate and calcium nitrate. It transforms into a system. Additionally, mineral residues containing phosphates are collected at the bottom of the combustion space. this The residue is phosphoric acid formed by combining oxides of sulfur and nitrogen with CaO. Calcium, nitrogen and phosphorus by mixing with calcium and calcium nitrate Feed with valuable fertilizers containing acid salts.

本発明は、例えば、農場に販売され、メタンを含む洗浄されたガスの排出部が頂 部にある向流式洗浄装置を有するプラントにも関し、その排出部はメタンを燃焼 するための燃焼装置に接続され、その燃焼装置は、出発材料の貯蔵空間中に存在 する加熱管に接続された燃焼ガス用排出部を有する。The present invention can be used, for example, to sell a farm to a farm where the exhaust of the cleaned gas containing methane is This also relates to plants with counter-current cleaning equipment located in the connected to a combustion device for It has a combustion gas outlet connected to a heating tube.

そのプラントは、肥料スラッジを収集及び運搬する船の上に配置することもでき る。The plant can also be located on a ship that collects and transports fertilizer sludge. Ru.

本発明による装置の特別な態様として、厩舎の空間も洗浄装置の底にあるガス供 給部に接続され、そのため普通であれば大気中に放出されるであろう排出舎内空 気中に存在していたアンモニア及び硫化水素がそこがら回収される。As a special embodiment of the device according to the invention, the stable space is also provided with a gas supply at the bottom of the cleaning device. The air inside the exhaust building is connected to the air supply and therefore would normally be released into the atmosphere. Ammonia and hydrogen sulfide present in the air are recovered therefrom.

もし望むならば、本発明による方法及び装置により農場で生じたアンモニア溶液 を、それから濃厚な純水アンモニア溶液が製造される中心地に輸送し、然る後、 その溶液を濃厚アンモニア溶液を必要とする場所へ輸送してもよい。If desired, the ammonia solution produced on the farm by the method and apparatus according to the invention is then transported to a center where a concentrated pure ammonia solution is produced; The solution may be transported to locations where concentrated ammonia solution is required.

本発明は、上で述べたようなプラントにも関し、そのプラントは、本発明の方法 に従い処理された肥料及び(又は)排泄物のための貯蔵サイロ、そのサイロから 供給装置により燃焼装置へその材料が供給でき、前記燃焼装置からの燃焼ガスの 排出部に接続された熱交換器、及び燃焼ガスからの硫黄及び窒素の酸化物のため の熱交換器に接続された酸化カルシウム床を有する容器を有する。The invention also relates to a plant as described above, which plant comprises the method according to the invention. storage silos for manure and/or excrement treated in accordance with; A supply device can supply the material to the combustion device, and the combustion gas from the combustion device can be supplied with the material. Heat exchanger connected to the exhaust, and for oxides of sulfur and nitrogen from the combustion gases a vessel with a bed of calcium oxide connected to a heat exchanger.

本発明を、本発明による装置の好ましい態様に関する図面に関連して更に説明す る。The invention will be further explained in connection with the drawings of preferred embodiments of the device according to the invention. Ru.

第1図に関し、肥料貯槽1(肥料ピット又はサイロ)中に加熱管2が配備されて いる。肥料ビット上のガスはポンプ3により排出され、それらは洗浄装置4中に 底がら導入される。この装置には上方へ行く程粒径が減少する複数の充填単位装 置(unit)の層が入っている。これらの層の上に開口6が開けられた水平パ イプ5が配置されている。ポンプ16はこのパイプに水を供給し、その水は例え ば、最高lO℃の温度を有する。洗浄装置4には、底に溢流パイプが配備されて おり、それを通って、洗浄装置4の底に収集されたアンモニア及び硫化水素を含 む水溶液が水酸化鉄スラッジ床8中へ底がら導入される。そこで硫化水素は硫化 鉄に転化する。アンモニア溶液はこの床の上から排出され保存される。Regarding Fig. 1, heating pipe 2 is installed in fertilizer storage tank 1 (fertilizer pit or silo). There is. The gases on the fertilizer bits are pumped out by a pump 3 and they are transferred into a cleaning device 4. It will be introduced from the bottom up. The device has several packing units with particle size decreasing upwards. It contains layers of units. A horizontal pattern with openings 6 above these layers Type 5 is placed. Pump 16 supplies water to this pipe, and the water is e.g. For example, it has a temperature of up to 10°C. The cleaning device 4 is equipped with an overflow pipe at the bottom. and through it the ammonia and hydrogen sulfide-containing gas collected at the bottom of the cleaning device 4. An aqueous solution of the iron hydroxide sludge is introduced into the iron hydroxide sludge bed 8 from the bottom. So hydrogen sulfide is sulfurized Converts into iron. The ammonia solution is drained over this bed and stored.

アンモニア及び硫化水素が殆ど除かれているが、がなりの量のメタンガスを含む ガスが燃焼装置9に送られ、そこでメタンを燃焼する。炉が始動又は消える時、 ガスバーナー10を用いて温度を、炉を通過するガス中のメタンが発火し、その ガス中の酸素により燃焼するような温度へ上昇させることができる。燃焼ガスは 、大気中へ放出される前に、ビット1中の肥料を加熱するのに少なくとも部分的 に用いられる。このなめ、それらをパイプ20を通って貯槽lの加熱用管2へ送 る。もし望むならば、それらのガス中に存在するCO2を、水酸化カルシウム溶 液にそのガス流を通過させることにより結合させてもよい。Most of ammonia and hydrogen sulfide are removed, but a considerable amount of methane gas is included. The gas is sent to a combustion device 9 where the methane is combusted. When the furnace starts or turns off, Using the gas burner 10, the temperature is set so that the methane in the gas passing through the furnace ignites and The oxygen in the gas can raise the temperature to the point where it burns. The combustion gas , at least partially to heat the fertilizer in Bit 1 before being released into the atmosphere. used for. This lick sends them through the pipe 20 to the heating pipe 2 of the storage tank l. Ru. If desired, the CO2 present in those gases can be dissolved in calcium hydroxide. The combination may be made by passing the gas stream through the liquid.

本発明による装置の代表的な態様として、舎内空気もパイプ12によって排出し 、次にその空気を肥料ピットから排出されたガス流と一緒に洗浄装置4中に送る 。In a typical embodiment of the device according to the invention, indoor air is also exhausted through the pipe 12. , which air is then sent into the cleaning device 4 together with the gas stream discharged from the fertilizer pit. .

この舎内空気は、厩舎内に配置されたパーイブで、調節可能な吸引バルブがその 全長に互って取付けられたパイプ15を通って調節可能な扇風機13によって厩 舎から排出される。This indoor air is supplied by a perve located inside the stable, which is controlled by an adjustable suction valve. Stables are provided by adjustable fans 13 through pipes 15 attached to each other along the entire length. It is discharged from the building.

第2図は、上述した装置を変更したものに関し、その場合、パイプ12を通って 排出され、肥料貯槽がら取り出されたガスから分離された舎内空気を第二の洗浄 装置4aへ送る。両方の洗浄装置4及び4Aでは、上方へ移動するガスは再循環 アンモニア溶液により洗浄され、その溶液は、水酸化鉄スラッジ床が存在する地 中に配置されたタンク11からポンプ16により送り出される、床8は地下水又 は水道水によって冷却され、その水はパイプ29を通って送られる。FIG. 2 relates to a modification of the device described above, in which case the pipe 12 is A second cleaning of the indoor air separated from the gas discharged and extracted from the fertilizer storage tank Send to device 4a. In both cleaning devices 4 and 4A, the upwardly moving gas is recirculated. The solution is washed with an ammonia solution and the solution is applied to the ground where the iron hydroxide sludge bed is present. The floor 8 is filled with ground water or water pumped by a pump 16 from a tank 11 located inside. is cooled by tap water, which is sent through pipe 29.

第1図及び第2図の両方の炉9中には管27が配備されており、それを通って水 を流すことができ、出発材料の加熱以外の目的、例えば農場内の集中暖房のため に過剰に生成した熱を利用することができる。一方向性バルブ39a及び33a には、燃焼炉から炎が逆流しないように防止ガーゼが配置されている。第2図中 の分岐管25Aは、もし望むならば、パイプ25を通って排出された洗浄された ガスの一部分をガス発生器へ送っても良いことを例示している。A tube 27 is provided in the furnace 9 of both FIGS. 1 and 2, through which water is passed. can flow for purposes other than heating the starting material, e.g. for central heating within the farm. The excess heat generated can be used to One-way valves 39a and 33a A protective gauze is placed in the furnace to prevent flames from flowing back from the combustion furnace. In Figure 2 The branch pipe 25A of This example illustrates that a portion of the gas may be sent to a gas generator.

パイプ20中には制御バルブ28が配備されており、貯槽1中の熱の必要量に従 って調節される。燃焼室9中のガス混合物の組成は、制御バルブ30によって調 節することができる。A control valve 28 is provided in the pipe 20 to control the amount of heat required in the storage tank 1. It is adjusted. The composition of the gas mixture in the combustion chamber 9 is regulated by a control valve 30. It can be divided into sections.

第3図は、第1図及び第2図の装置を更に発展させたもので、燃焼炉9中で過剰 の肥料を燃焼することができるようにしたものに関する。Fig. 3 shows a further development of the apparatus shown in Figs. 1 and 2, in which excess Contains fertilizers that can be burned.

このプラントでは、過剰の肥料を収集容器21中に入れる。肥料ピット1(第1 図及び第2図)中で本発明の方法に従い処理されたこの肥料は、約30重量%の 水分含有量を有する。肥料ピット1中では二つの層が形成され、加熱によってメ タン及び他のガスが引き出された後、上の層は約70重量%の固形物含有量を有 する。肥料ビット中の燐酸塩の大部分はこれら上の層中で終わっている。In this plant, excess fertilizer is placed in a collection container 21. Fertilizer pit 1 (1st This fertilizer treated according to the method of the invention in Figs. It has a moisture content. Two layers are formed in the fertilizer pit 1, and the fertilizer is heated. After the tunic and other gases are drawn off, the top layer has a solids content of about 70% by weight. do. Most of the phosphate in the fertilizer bit ends up in these upper layers.

下のもっと液体状の層は燐酸塩含有量が遥かに少なく、最終的にはそれを脱燐し た後排出される。The lower, more liquid layer has much less phosphate and will eventually dephosphorize it. It is then discharged.

燐酸塩含有量の遥かに高い上の層が直接地面に肥料として用いられない限り、そ れを容器21中に運び込む。この容器から乾燥肥料を運搬機22により燃焼炉9 中に導入する。肥料の鉱物残渣は灰として炉の底にある火格子22を通って落下 する。これらの灰は燐酸塩及び珪酸塩からなる。燃焼炉9中での肥料の燃焼によ り、硫黄酸化物及び窒素酸化物も生成する。環境に対して非常に有害なことにな るこれらの酸化物が大気中へ流出するのを防ぐために、硫黄及び窒素の酸化物を 含有する高温燃焼ガスを酸化カルシウムの床17に通す。この酸化カルシウムは 硫黄及び窒素の酸化物を燐酸カルシウム及び硝酸塩カルシウムへ転化する。熱回 収装置18及び塵フィルター19が燃焼炉9と酸化カルシウム床17の間に配置 されている。熱交換器中では循環水が加熱され、炉9からの燃焼ガスが冷却され る。酸化カルシウム床の下の塵フィルター19中で、塵は燃焼ガスから除去され 、然る後、このガスは酸化カルシウム床19を通過する。もし望むならば、床1 9の酸化カルシウムは石灰石(CaC○、)をか焼することにより生成させるこ とができる。その場合、例えば水軟水化装置から生じたカルサイト粒子(僅か0 .5%の水しか含まないCa CO* )を−、燃焼すべき肥料と一緒に類9中 に導入することができる。これらの粒子は炉中に行き亙っている高温でか焼され る。形成されたCaOを、炉底中の肥料鉱物成分と一緒に収集する。CaO、燐 酸塩及び珪酸塩の混合物は、燃焼ガス中の硫黄及び窒素の酸化物を結合するため の床I9に用いることができる。これはCaOを燐酸カルシウム及び硝酸カルシ ウムに転化する結果になる。燐酸塩、Vl、酸塩、硝酸塩、及びカルシウム生成 物の混合物は肥料として用いてもよい。Unless the upper layer, which has a much higher phosphate content, is applied directly to the ground as fertilizer, This is carried into the container 21. The dry fertilizer is transferred from this container to a combustion furnace 9 by a transporter 22. Introduce it inside. The mineral residues of the fertilizer fall as ash through the grate 22 at the bottom of the furnace. do. These ashes consist of phosphates and silicates. By burning the fertilizer in the combustion furnace 9 Sulfur oxides and nitrogen oxides are also produced. very harmful to the environment oxides of sulfur and nitrogen to prevent these oxides from escaping into the atmosphere. The hot combustion gases contained therein are passed through a bed 17 of calcium oxide. This calcium oxide Converts sulfur and nitrogen oxides to calcium phosphate and calcium nitrate. heat cycle A collection device 18 and a dust filter 19 are arranged between the combustion furnace 9 and the calcium oxide bed 17. has been done. In the heat exchanger, the circulating water is heated and the combustion gas from the furnace 9 is cooled. Ru. Dust is removed from the combustion gases in a dust filter 19 below the calcium oxide bed. , after which this gas passes through a bed of calcium oxide 19. floor 1 if you want Calcium oxide in No. 9 can be produced by calcining limestone (CaC○,). I can do it. In that case, for example, calcite particles (only 0 .. Ca CO*), which contains only 5% water, is combined with the fertilizer to be burned in Category 9. can be introduced into These particles are calcined at high temperatures prevailing in the furnace. Ru. The formed CaO is collected together with the fertilizer mineral components in the hearth bottom. CaO, phosphorus Mixtures of acid salts and silicates to bind sulfur and nitrogen oxides in the combustion gases It can be used for floor I9. This converts CaO into calcium phosphate and calcium nitrate. This results in conversion to um. Phosphate, Vl, acid salt, nitrate, and calcium production The mixture may be used as a fertilizer.

第3図によるプラントでは、熱交換器中で加熱された水は、導管20を通ってサ イロ1中の加熱用管中へ送られ(第1図及び第2図参照)、その中の肥料を加熱 し、更に、例えば集中暖房装置30又はボイラー31の加熱に用いてもよい。In the plant according to FIG. 3, the water heated in the heat exchanger passes through conduit 20 to the The fertilizer is sent to the heating pipe in Iro 1 (see Figures 1 and 2) and heats the fertilizer inside. However, it may also be used, for example, to heat a central heating device 30 or a boiler 31.

洗浄塔から来たCH,ガスもガス発生器の燃焼機関24のために用いる場合には 、導管25を通って供給されたこのCH4ガスを、厩舎から取り出され、洗浄塔 で洗浄され、導管26を経て供給されたC H4+ 02 + N 2のガス混 合物と、ガス発生器のタービンの金属がそのガス流中の窒素酸化物によって腐食 されるのを防ぐなめ、予め混合することはしない。When CH and gas coming from the cleaning tower are also used for the combustion engine 24 of the gas generator, , this CH4 gas supplied through conduit 25 is taken out from the stable and sent to the washing tower. The gas mixture of C H4 + 02 + N2 supplied via conduit 26 metals in the gas generator turbine are corroded by nitrogen oxides in the gas stream. Do not pre-mix to prevent licking.

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Claims (12)

【特許請求の範囲】[Claims] 1.環境に有害なメタン及び他の化学物質が放出される材料を処理する方法にお いて、前記材料を加熱し、放出されるガスを水又は化学的ガス洗浄循環溶液で洗 浄処理にかけ、洗浄装置から放出されるガス中のメタンを燃焼し、発生する熱を 少なくとも部分的に出発材料を加熱するのに用いることを特徴とする処理方法。1. How to process materials that release methane and other chemicals that are harmful to the environment. The material is then heated and the released gas is washed with water or a chemical gas cleaning circulation solution. During the cleaning process, methane in the gas emitted from the cleaning equipment is burned, and the heat generated is A processing method characterized in that it is used to at least partially heat the starting material. 2.出発材料がアンモニアを含有し、洗浄が循環アンモニア溶液で行われること を特徴とする請求項1に記載の方法。2. The starting material contains ammonia and the washing is carried out with circulating ammonia solution. A method according to claim 1, characterized in that: 3.出発材料(一種又は多種)として肥料及び(又は)排泄物を用いることを特 徴とする請求項2に記載の方法。3. Particularly with the use of fertilizers and/or excreta as starting material(s). 3. The method according to claim 2, wherein: 4.家畜の住む厩舎から取り出された舎内空気を水又は循環アンモニア溶液と同 時に、肥料及び(又は)排泄物を加熱する空間から抽出されたガスで洗浄処理す ることを特徴とする請求項3に記載の方法。4. The indoor air extracted from stables where livestock live is treated with water or a circulating ammonia solution. Sometimes the manure and/or excreta are cleaned with gas extracted from the heating space. 4. The method according to claim 3, characterized in that: 5.出発材料が排水汚泥であることを特徴とする請求項2に記載の方法。5. 3. Process according to claim 2, characterized in that the starting material is wastewater sludge. 6.12℃を越えない温度を有する洗浄液体を用いて洗浄することを特徴とする 請求項1〜5のいずれか1項に記載の方法。6. Characterized by cleaning with a cleaning liquid having a temperature not exceeding 12°C A method according to any one of claims 1 to 5. 7.洗浄中に得られたアンモニア溶液中に存在する硫化水素を、その溶液から水 酸化鉄スラッジにその溶液を通すことにより除去することを特徴とする請求項2 〜6のいずれか1項に記載の方法。7. The hydrogen sulfide present in the ammonia solution obtained during cleaning is removed from the solution by water. Claim 2, characterized in that the iron oxide sludge is removed by passing the solution through it. 7. The method according to any one of . 8.請求項1の方法に従い加熱された出発材料も、メタンが燃焼される燃焼炉中 で燃焼し、然る後、燃焼ガスを熱交換器で冷却し、酸化カルシウム床に通して硫 黄及び窒素の酸化物を結合し、然る後、それらガスを大気中に放出することを特 徴とする請求項1〜7のいずれか1項に記載の方法。8. The starting material heated according to the method of claim 1 is also placed in a combustion furnace in which methane is combusted. The combustion gas is then cooled in a heat exchanger and passed through a bed of calcium oxide to produce sulfur. It is characterized by combining yellow and nitrogen oxides and then releasing these gases into the atmosphere. 8. The method according to any one of claims 1 to 7, wherein: 9.燃焼ガス中の硫黄及び窒素の酸化物と酸化カルシウムとの反応により形成さ れた硫酸カルシウム及び硝酸カルシウムを、炉の底から排出された燐酸塩含有残 渣と混合し、カルシウム、燐酸塩及び窒素を含有する肥料を得ることを特徴とす る請求項8に記載の方法。9. Formed by the reaction of sulfur and nitrogen oxides in combustion gases with calcium oxide. Calcium sulfate and calcium nitrate are removed from the phosphate-containing residue discharged from the bottom of the furnace. Characterized by mixing with residue to obtain fertilizer containing calcium, phosphate and nitrogen 9. The method according to claim 8. 10.請求項1〜9のいずれか1項に記載の方法を実施するためのプラントにお いて、メタンを含む洗浄されたガスの排出部が頂部にある向流式洗浄装置を有し 、その排出部はメタンを燃焼するための燃焼装置に接続され、その燃焼装置が、 出発材料の貯蔵空間中に存在する加熱管に接続された燃焼ガス用排出部を有する ブラント。10. A plant for carrying out the method according to any one of claims 1 to 9. It has a counter-current scrubber with an outlet for the scrubbed gas containing methane at the top. , its discharge part is connected to a combustion device for burning methane, and the combustion device with an outlet for the combustion gases connected to the heating pipes present in the storage space of the starting material Brandt. 11.厩舎も洗浄装置又は別の洗浄装置の底にあるガス供給部に接続され、該洗 浄装置かちの放出ガスが燃焼装置へ供給される請求項10に記載のブラント。11. The stable is also connected to the gas supply at the bottom of the cleaning device or another cleaning device and 11. A blunt according to claim 10, wherein the exhaust gas from the purification device is fed to a combustion device. 12.請求項1に記載の方法に従い処理された肥料及び(又は)排泄物のための 、それら材料を供給装置により燃焼装置へ供給できる貯蔵サイロ、前記燃焼装置 からの燃焼ガスの排出部に接続された熱交換器、及び燃焼ガスからの硫黄酸化物 及び窒素酸化物を除去するための、熱交換器に接続された酸化カルシウム床を有 する容器を特徴とする請求項10又は11に記載のプラント。12. For fertilizer and/or excrement treated according to the method of claim 1. , a storage silo capable of supplying these materials to a combustion device by means of a feeding device, said combustion device a heat exchanger connected to the outlet of the combustion gases from the combustion gases, and sulfur oxides from the combustion gases; and a calcium oxide bed connected to a heat exchanger to remove nitrogen oxides. The plant according to claim 10 or 11, characterized by a container for.
JP2511502A 1989-08-15 1990-08-15 Methods and apparatus for treating materials from which methane and other chemicals harmful to the environment are released Pending JPH04507217A (en)

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MY143253A (en) 2002-08-01 2011-04-15 Gfe Patent As Method and device for stripping ammonia from liquids

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DE3709521A1 (en) * 1986-05-06 1987-11-12 Ilka Luft & Kaeltetechnik Process and device for combined purification of flue gas and animal house air
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