JPS61111948A - Apparatus for manufacturing cement clinker with small alkalicontent - Google Patents
Apparatus for manufacturing cement clinker with small alkalicontentInfo
- Publication number
- JPS61111948A JPS61111948A JP60227962A JP22796285A JPS61111948A JP S61111948 A JPS61111948 A JP S61111948A JP 60227962 A JP60227962 A JP 60227962A JP 22796285 A JP22796285 A JP 22796285A JP S61111948 A JPS61111948 A JP S61111948A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- water
- flue gas
- preheater
- pipe
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000004568 cement Substances 0.000 title claims description 24
- 238000004519 manufacturing process Methods 0.000 title description 7
- 239000007789 gas Substances 0.000 claims description 49
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 49
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 30
- 239000003546 flue gas Substances 0.000 claims description 30
- 239000003513 alkali Substances 0.000 claims description 13
- 239000010802 sludge Substances 0.000 claims description 12
- 238000009423 ventilation Methods 0.000 claims description 12
- 238000002347 injection Methods 0.000 claims description 6
- 239000007924 injection Substances 0.000 claims description 6
- 238000000746 purification Methods 0.000 claims description 6
- 238000000605 extraction Methods 0.000 claims description 4
- 239000013505 freshwater Substances 0.000 claims description 4
- 239000003814 drug Substances 0.000 claims 1
- 229940079593 drug Drugs 0.000 claims 1
- 239000000428 dust Substances 0.000 description 10
- 239000000203 mixture Substances 0.000 description 9
- 150000001875 compounds Chemical class 0.000 description 8
- 238000004140 cleaning Methods 0.000 description 7
- 238000001035 drying Methods 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 238000001816 cooling Methods 0.000 description 6
- 239000006227 byproduct Substances 0.000 description 4
- 238000010304 firing Methods 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- 238000010276 construction Methods 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 239000007792 gaseous phase Substances 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 239000007791 liquid phase Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 description 2
- 235000012239 silicon dioxide Nutrition 0.000 description 2
- 238000005245 sintering Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 230000007704 transition Effects 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000004088 foaming agent Substances 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- -1 pH adjusters Substances 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- 239000004094 surface-active agent Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B7/00—Hydraulic cements
- C04B7/36—Manufacture of hydraulic cements in general
- C04B7/60—Methods for eliminating alkali metals or compounds thereof, e.g. from the raw materials or during the burning process; methods for eliminating other harmful components
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Structural Engineering (AREA)
- Toxicology (AREA)
- Public Health (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
- Treating Waste Gases (AREA)
- Manufacture And Refinement Of Metals (AREA)
- Incineration Of Waste (AREA)
- Compounds Of Unknown Constitution (AREA)
- Feeding, Discharge, Calcimining, Fusing, And Gas-Generation Devices (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】
この発明は乾燥方法及び半乾燥方法によってセメントを
製造する方法及びアルカリ含有で且つ他の有害物質を含
む原料及び有害物質含有燃料から成るアルカリの少ない
セメントクリンカの製造装置に関する。この発明は特に
予熱器、ロータリーキルン、冷却器を用いるセメントク
リンカの焼成に適している。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing cement by a drying method and a semi-drying method, and an apparatus for producing cement clinker with a low alkali content, which is made of a raw material containing alkali and other harmful substances, and a fuel containing harmful substances. . The invention is particularly suitable for firing cement clinker using preheaters, rotary kilns, and coolers.
セメント製造111の原料は地質学的条件に応してアル
カリ化合物、塩素化合物、硫黄化合物を一定量含んでい
る。更にこれは必要な燃料についても言える。これらの
薬品は熱いキルン領域、特に焼結域でセメントクリンカ
WA造の際に気化し、排ガス流と共に予Sl器の方向に
運ばれる。キルノ系のより冷たい領域でこれらの化学的
化合物は凝縮し、材料流と共に再び焼結域内に入る。そ
の場合内部循環の結果アルカリ化合物が増加し、このア
ルカリ化合物は予熱器中に粘りけのある塵をためるか−
1たけ沈澱させ、生産されたセメントでは品質低トとい
う結果をムたら4°。Raw materials for cement production 111 contain certain amounts of alkali compounds, chlorine compounds, and sulfur compounds depending on geological conditions. This also applies to the fuel required. These chemicals are vaporized during cement clinker WA production in the hot kiln area, especially the sintering area, and are carried along with the exhaust gas stream in the direction of the preslitter. In the colder regions of the Kirno system these chemical compounds condense and enter the sintering zone again with the material flow. In that case, as a result of internal circulation, alkaline compounds increase, and these alkaline compounds accumulate sticky dust in the preheater.
After 1 degree precipitation, the quality of the produced cement was 4 degrees.
周知のように、非晶質または可溶性の珪酸を含む一定の
骨材は、使用したセメントが0.6マスバーセントのN
atO当Qiを(イする場合にのみコンクリートに加工
4゛ることかできる。というのはその池の場合にはコン
クリートはアルカリ駆逐によって破壊されるからである
。これは、非晶質または可溶性の形の珪酸を存する骨材
のある帯域に対して有利なのは使用されるセメントのア
ルカリ含有’+tがセメント製造時に0.6マスパーセ
ントNatO当量に低下するからである。As is well known, certain aggregates containing amorphous or soluble silicic acid contain 0.6 mass percent N of the cement used.
It is possible to process concrete into concrete only if atO and Qi are This is advantageous for certain zones of aggregates containing silicic acid in the form of silica, since the alkali content of the cement used is reduced to 0.6 mass percent NatO equivalent during cement production.
技術水車によれば、セメントクリツカのアルカリ含イ「
…の減少はいわゆるバイパス系によって起こることがあ
る。その場合′Y−熱器とロータリーキルンの間の移行
域では、排ガス(煙道ガス)の一部またはロータリーキ
ルンの全排ガス量を装置から取出し、脱塵し、再び装置
に戻すかまたは大気中に吹放つことによって中断されろ
。集積する塵は投棄されろ。According to Technical Hydrogen, the alkaline content of cement kritka is ``
A decrease in ... can occur through the so-called bypass system. In that case, in the transition zone between the Y-heater and the rotary kiln, part of the exhaust gas (flue gas) or the entire amount of exhaust gas from the rotary kiln is removed from the installation, dedusted and returned to the installation again or blown into the atmosphere. Be interrupted by releasing. Dump the dust that accumulates.
ガスはアルカリ化合物ができる限りガス状であって塵濃
度を低くしてある箇所でキルンから取出され、その後冷
気によって強力に冷却されろ。その場合問題なのは、塵
が冷却装置、!の壁部に接触し[tつ、接着現象または
沈澱を防ぐためにアルカリ化合物が冷却装置に至るまで
に凝縮するのを防[1−することである。冷却の後通常
はバイパス・ガスの湿IFI(コンディンヨニング)が
行なわれて、続いて電気式ガス浄化装置中で脱塵を実施
することができる。次に冷却されたバイパスガスは直接
大気中に運ばれるかまたは予熱器後方でキルン装置の煙
道ガスに供給される。The gas is removed from the kiln at a point where the alkaline compounds are as gaseous as possible and the dust concentration is low, and then it is strongly cooled with cold air. In that case, the problem is dust in the cooling system! The purpose is to prevent alkali compounds from condensing on the way to the cooling device in order to prevent adhesion or precipitation. After cooling, a wet IFI (condensation) of the bypass gas is usually carried out, and subsequent dedusting can be carried out in an electric gas purification system. The cooled bypass gas is then conveyed directly to the atmosphere or fed to the flue gas of the kiln unit after the preheater.
以上の問題については、ドイツ連邦共和国公開2335
045、同2613610号公報、ドイツ連邦共和国特
許2708486C号公報、ドイツ連邦J!、和国出願
公開2742099号及び同2838692号公報に記
載かある。Regarding the above issues, please refer to the publication of the Federal Republic of Germany 2335
045, Publication No. 2613610, Federal Republic of Germany Patent No. 2708486C, Federal Republic of Germany J! , is described in Japanese Patent Publication No. 2742099 and Japanese Publication No. 2838692.
技術水車によって公知の、アルカリの少ないセメントク
リツカの製造装置と設備は構造と装備に費用がかかる。The equipment and equipment for the production of low-alkali cement kritkas known from the technical water mills are expensive in construction and equipment.
これら公知のものの更に欠点なのは、アルカリ化合物が
既にガスの吸引の前に凝縮し1つ塵に付着している場合
には運転困難なことである。それは特にトIss、so
w、NOxのような有害物質の排ガスの処理がないかま
たは不満足なこと、熱消費総量の50%になる熱損失、
セメノドクリンカ焼成装置の外側での消費に使う二次空
気の非利用である。A further disadvantage of these known devices is that they are difficult to operate if the alkaline compounds are already condensed and deposited on the dust before the gas is drawn in. That's especially true
w, no or unsatisfactory treatment of hazardous exhaust gases such as NOx; heat losses amounting to 50% of total heat consumption;
This eliminates the use of secondary air for consumption outside the semenodo clinker calciner.
この発明の目的は、アルカリの少ないセメントクリツカ
を多争に生産し且つ環境になじむように製造するごとが
できろ筒中で1つ廉価な装置の開発にある。この装置は
集積ずろ副産物をfす用可能な形に転換して1つ二次空
気の利用をIIT能にする。The object of the present invention is to develop an inexpensive device that can produce cement concrete with a low alkali content in a manner that is compatible with the environment. This device converts the accumulated by-products into a usable form, making the use of secondary air possible.
この発明の1λ木課題は、アルカリの少ないセメントク
リツカを製造するための装置の開発にある。The object of this invention is to develop an apparatus for producing cement concrete with low alkali content.
この装置では、750℃以上の煙道ガスから有害成分、
特にアルカリ化合物、またはS Oe、 Hrs −N
Ox、C1と塵をも除去される。This device removes harmful components from flue gas at temperatures of 750°C or higher.
Especially alkaline compounds, or S Oe, Hrs -N
Ox, C1 and dust are also removed.
この課題は次のようにして達成される。即ち予熱器から
ロータリーキルンに至るまでの帯域で煙道ガス取出し位
置に洗浄流体、特に水で運転されろ、ポンプを有する放
水反応器を設けてあり、煙道ガス取出し口の向かい側の
端部に捕集容器が接続しており、この捕集容器は新水供
給用ボールタップ、薬品供給装置、純ガス排出管を有す
る。この純ガス排出管から支持換気扇を組み入れである
純ガス管が予熱器煙道ガス管に通じている。純ガス管は
支持換気扇の後方に大気中に出る純ガス排出口を有する
。This task is accomplished as follows. That is, in the zone from the preheater to the rotary kiln, a water discharge reactor with a pump operated with cleaning fluid, in particular water, is provided at the flue gas take-off location, and at the end opposite the flue gas take-off there is a water discharge reactor with a pump. A collection vessel is connected, which has a ball tap for supplying fresh water, a chemical supply device, and a pure gas discharge pipe. From this pure gas discharge pipe a pure gas pipe incorporating a supporting ventilation fan leads to the preheater flue gas pipe. The pure gas pipe has a pure gas outlet to the atmosphere behind the support ventilation fan.
純ガス管と予熱器煙道ガス管とは合体0で煙道ガス混合
管になり、この煙道ガス混合管は煙道ガス換気扇を介し
て電子フィルタに通じている。The pure gas pipe and the preheater flue gas pipe combine to form a flue gas mixing pipe, which leads to the electronic filter via a flue gas ventilation fan.
送り・戻し管を有する熱交換器がある捕集容器には冷却
器を装備できろスラッノ分離装置がポンプと共に後置接
続されている。スラッジ除去にはスラッノ分離器を有す
る水回路を別に設けろことらできる。The collecting vessel, which has a heat exchanger with feed and return pipes, can be equipped with a cooler and is downstream connected to a Surano separator together with a pump. Sludge removal can be accomplished by providing a separate water circuit with a Surano separator.
捕集容器はまた、たとえば二重ノヤケツト構造によって
熱交換器としてさえも構成することができる。The collection vessel can also be constructed as a heat exchanger, for example by means of a double jacket construction.
アルカリの少ないセメントクリツカを製造するこの新規
な装置は、煙道ガス取出し位置で噴射水反応器が(起こ
す負圧によっていわゆるバイパスガスとして煙道ガスが
取出されるように機能する。This new device for producing low-alkali cement concrete works in such a way that the flue gas is withdrawn as a so-called bypass gas by means of the negative pressure created by the injection water reactor at the flue gas withdrawal location.
その場合洗浄水と取出された煙道ガスの間で、突状で、
強力で1つ完全な熱と物質の交換が行なわイ1て洗浄水
とガスが回し温度になり、塵と水溶性の薬品かガスの形
から水相に移行し、Sotが塵のCaOに結ばれる。ア
ルカリは大部分が水に溶け[Lつ残りの部分は不溶の残
留物中に含まれている。In that case, between the cleaning water and the removed flue gas, a convex,
A strong and complete heat and mass exchange takes place. 1) The cleaning water and gas are brought to temperature, the dust and water-soluble chemicals or gases are transferred to the water phase, and the Sot binds to the CaO in the dust. It will be done. Most of the alkali is soluble in water; the remaining portion is contained in the insoluble residue.
噴射水反応器からは洗浄水と残りの湿った煙道ガスから
成る混合物が熱交換と物質交換の後直接捕集容器中に導
入される。この捕集容器中では密1y差によってこの混
合物の分離が行なわれ、固体1戊分が沈澱ずろ。From the jet water reactor, the mixture of wash water and remaining moist flue gas is introduced directly into the collection vessel after heat and mass exchange. In this collection vessel, the mixture is separated by a difference in density, and one portion of the solid is precipitated.
噴射水反応器に併設されているポンプからは捕集容器か
らくる洗浄水が吸引され、循環して噴射水反応器を介し
て再び捕集客器に供給される。Washing water coming from the collection container is sucked through a pump attached to the jet water reactor, circulated, and supplied to the collection container again via the jet water reactor.
固体残留物の沈澱に応じて噴射水反応器に供給された全
水量がスラ1)分離器を介して捕集容器から取出されろ
かまたはスラッノ除去が別設備の水回路によって行なわ
れる。水回路中にはスラゾノ分離器が結合されている。Depending on the precipitation of the solid residue, the total amount of water fed into the water injection reactor is removed from the collection vessel via a sludge 1) separator, or sludge removal is carried out by a separate water circuit. A slazono separator is connected in the water circuit.
スラッノ分離器からはスラッジの他に浄化された洗浄水
が出てくる。洗浄水は場kによっては再び加熱される。In addition to sludge, purified wash water comes out of the Surano separator. The wash water may be heated again depending on the location.
洗浄水を再生ずるためにその回路にpH値調整剤、フロ
ブク化剤、表面活性剤のような薬品を投入ずろ。In order to regenerate the wash water, chemicals such as pH adjusters, foaming agents, and surfactants should be added to the circuit.
この装置によってアルカリ含有!■が0.6マスパーセ
ントのNano当量と同じかまたはそれより少ないセメ
ントクリツカを製造することかできろ。This device contains alkali! Is it possible to produce a cement concrete with a nano equivalent of 0.6 mass percent or less?
その場合できた副産物は再びセメント製造のために、あ
るいはたとえば肥料として使用することができる。二次
熱を利用するために、捕集容器中に設けられた熱交換器
または熱交換器として構成された捕集客器を配百によっ
てたとえば暖房装置に連結オろことができる。The resulting by-products can then be used again for cement production or, for example, as fertilizer. In order to utilize the secondary heat, a heat exchanger installed in the collection vessel or a collection device configured as a heat exchanger can be connected to a heating device, for example, by means of a power supply.
実施例 二つの実施例を示した図について詳記ずろ。Example Please provide detailed information regarding the figures showing the two embodiments.
第一の例(第1図の半乾燥法)ではa−タリーキルン1
と火床予熱42との間にある煙道ガス取出し位置3に噴
射水反応器4を配設してある。この噴q・f水反応器4
は捕集容器5に通しており、この捕集客器は送り・戻し
導管13を有する二次エネルギー111用のための熱交
換器I4、フロート弁15.4品供給器I9をもってい
るヮ捕集客器5には洗浄水導管20が接続して」jす、
この導管中にポンプ12と熱交換器17を配設してある
。更に浄化管25が捕集容器5に接続しており、浄化管
中にはスラノノ分離と(10、ポンプ18、熱交換器1
7か配設されているウスラッノ分#器10は冷却器16
を備えている。噴射水反応器4中では循環中にポンプで
汲んだ洗aト水によって負圧か生しろ、。In the first example (semi-drying method shown in Figure 1), a-tally kiln 1
An injection water reactor 4 is arranged at the flue gas take-off position 3 between the preheater and the grate preheater 42 . This jet q/f water reactor 4
is passed through a collection vessel 5, which has a heat exchanger I4 for secondary energy 111 with a feed/return conduit 13, a float valve 15, and a four-product feeder I9. A cleaning water conduit 20 is connected to 5.
A pump 12 and a heat exchanger 17 are arranged in this conduit. Furthermore, a purification pipe 25 is connected to the collection container 5, and in the purification pipe there are installed a suranono separation (10, a pump 18, a heat exchanger 1).
The Usurano fractionator 10, which is installed in
It is equipped with In the injection water reactor 4, a negative pressure is created by the washing water pumped during circulation.
これによって煙道ガスが取出し位置3で火床予熱器2か
ら吸出され且つこの吸出工程の結果洗浄水としての循環
ポンプ水と゛バイパスガスとの間で突然且つ強力な熱・
物質交換か行なわれる。この水・煙道ガス混合物は捕集
容器5中に導入され、この容器の中で密度差に基づいて
混合物が分離されて液状且つガス状の相に転換する。環
境汚染成分から遥かに遠く離れている、湿気のある冷却
されたバイパスガスは浄化排気管6を経て捕集容器から
出て、純ガス配管21中の支持換気扇7によって純ガス
排出口24から大気中に放出されるかまたは処理のため
に予熱器煙道ガス管22に入れられるかして、その後神
道ガス混合物は煙道ガス換気扇8と煙道ガス混合管23
を経て電子フィルタ9中に導入される。This causes the flue gas to be sucked out of the grate preheater 2 at the extraction point 3, and as a result of this suction process there is a sudden and intense heat exchange between the circulating pump water as cleaning water and the bypass gas.
An exchange of substances takes place. This water/flue gas mixture is introduced into a collection vessel 5 in which the mixture is separated on the basis of density differences and converted into liquid and gaseous phases. The humid and cooled bypass gas, which is far away from the environmental pollutants, exits the collection vessel via the purifying exhaust pipe 6 and is discharged to the atmosphere from the pure gas outlet 24 by the supporting ventilation fan 7 in the pure gas pipe 21. The Shinto gas mixture is then discharged into the flue gas ventilation fan 8 and the flue gas mixing pipe 23 for treatment.
It is introduced into the electronic filter 9 through the.
洗浄水またはその一部は捕集容器から取出されて液体サ
イクロン10から導出され、スラッノ分離の後洗浄水循
環によって浄化された洗浄水が加熱され「Lつポンプ1
8によ−・て捕集容器5中にがされる熱交換器17を経
−ご案内される。装置中の水量を一定に保つために、フ
ロート弁I5を介して捕集容器5に新水を供給する。こ
の断水は予め液体サイクロノ10の冷却W+6に利用し
て、水溶性ガス成分を分11jl−J°るために濃度差
を作り出す。The wash water or a part thereof is taken out from the collection container and led out from the hydrocyclone 10, and after Surano separation, the purified wash water is heated by the wash water circulation and sent to the "L pump 1".
8 is guided through the heat exchanger 17 which is discharged into the collecting container 5. In order to keep the amount of water in the device constant, fresh water is supplied to the collection container 5 via the float valve I5. This water cutoff is used in advance for cooling W+6 of the liquid cyclone 10 to create a concentration difference in order to reduce the water-soluble gas component by 11jl-J°.
分離されたスラッジ11は面記各実施例に従って央にイ
J°効に処理されろ。The separated sludge 11 is then treated centrally according to the embodiments described below.
第二実施例(第2図の乾燥法)によれば噴射水反応器4
は竪型予熱器2とロータリーキル/lの間の移行部の煙
道ガス取出11位置3に配、没してある。According to the second embodiment (drying method in FIG. 2), the jet water reactor 4
is located at position 3 of the flue gas outlet 11 at the transition between the vertical preheater 2 and the rotary kill/l and is recessed.
噴射水反応器4は耐火性であり、捕集容器5に通し、て
おり、この捕集客器には二次空気利用のための熱交換7
514 、送り・戻し導管13、フロードブF15を備
えている。洗浄水導管20には液体サイクτノ:/10
のスラッジ分離のためと噴射水反応器4の駆動のために
ポンプ12を配設してある。The jet water reactor 4 is fireproof and passes through a collection vessel 5, which includes a heat exchanger 7 for the utilization of secondary air.
514, a sending/returning conduit 13, and a flow pipe F15. The cleaning water conduit 20 has a liquid cycle τ: /10.
A pump 12 is provided for sludge separation and for driving the jet water reactor 4.
噴射水反応器4の中には循環中にポンプで吸い1−げら
れた洗浄水によって負圧が生じる。A negative pressure is created in the jet water reactor 4 by the pumped wash water during circulation.
このよっにして煙道ガス取出し位置3でバイパスガス数
比しか行なわれろ。結果としてガスと洗aト水とが深く
混合され、両媒体の間に強力で且つ完全な熱・物質交換
が行なわれろ。続いて水・バイパス・混合物が捕集容器
5に導入され、この捕集容器中では密度差によってガス
状相が液状相から分離する。この後、浄化されて湿−1
で1jつ冷却されたバイパスガスは純ガス排出管6を経
て捕集容45から逃げ、その場合純ガス導管21中で支
持換気扇7によってガス供給が行なわれる。浄化され且
つ冷却されたバイパスガスは竪型予熱器ガスの処理に使
われる。この目的のために純ガス導管21は予熱器煙道
ガス導管22に通じている。In this way, only a bypass gas number ratio is performed at the flue gas removal location 3. As a result, the gas and wash water are deeply mixed, and there is a strong and complete heat and mass exchange between the two media. The water-bypass mixture is then introduced into the collection vessel 5, in which the gaseous phase is separated from the liquid phase due to density differences. After this, it is purified and moistened.
The bypass gas, which has been cooled by 1j, escapes from the collection volume 45 via the pure gas discharge line 6, in which case the gas supply is carried out in the pure gas line 21 by means of a supporting ventilation fan 7. The purified and cooled bypass gas is used to treat the vertical preheater gas. For this purpose, the pure gas line 21 leads into a preheater flue gas line 22.
このようにして作り出されたガス混合物は煙道ガス換気
扇8によって煙道ガス混合物導管23中を電子フィルタ
9まで給送されろ、このようにして、従来技術水撃で応
用されてきた乾燥ロータリーキルンの予熱器排ガスの高
価な処理を省くことができる。装置中の水1を一定に保
つために、新水がフロート弁15軽由で捕集容器5にU
I:給される。The gas mixture thus created is conveyed by a flue gas ventilation fan 8 in a flue gas mixture conduit 23 to an electronic filter 9, in this way the drying rotary kiln which has been applied in prior art water hammers. Expensive treatment of preheater exhaust gas can be omitted. In order to keep the water 1 in the device constant, fresh water is pumped into the collection container 5 via the float valve 15.
I: Provided.
乾燥法によるセメント製造の際のバイパスガスの塵濃度
は半乾燥法によるセメント製造の場合より大きいので、
液体サイクロン1oが捕集容器5とポツプ12との間に
配設され、冷却を必要としない。というのは抜き出され
f二全のスラッジ11によって可溶性成分の飽和以上の
増加が回避されるからである。The dust concentration in the bypass gas when producing cement using the dry method is higher than when producing cement using the semi-dry method.
A hydrocyclone 1o is arranged between the collection container 5 and the pop 12 and does not require cooling. This is because the extracted sludge 11 prevents the soluble components from increasing beyond saturation.
この発明の特別の利点は、セメントクリンカのアルカリ
含Y1°量の僅少なこと、装置各部の構成と装備技術に
かかる投資額が総体的に低いこと、特に、高価な処理設
備と付加バイパス・ガスフィルタの省略、それに伴う対
応セメントクリンカ焼成装置の設置に必要な空間の少な
さ、塵とバイパスガスから出るSO3の完全な除去、環
境改善する作業力式箋である。Particular advantages of the invention are the low alkali content Y1° of the cement clinker, the overall low investment in the construction and equipment technology of the various parts of the equipment, in particular the expensive processing equipment and additional bypass gas. This eliminates the need for a filter, reduces the space required to install the corresponding cement clinker firing equipment, completely removes SO3 from dust and bypass gas, and improves the working environment.
−りの大きな利点の本質は、元来短い配管路が付加され
ず、当該ユニット中に粘着する塵性澱物か生ぜす、二の
ようにして従来の設備に比較して運転故障がないために
この発明による装置の効果的ム作動@様が保証されてい
ることである。- The essence of the major advantages of this system is that it does not require the addition of short piping lines, and there are no operational failures compared to conventional equipment, such as the generation of dusty sludge that sticks to the unit. Effective operation of the device according to the invention is guaranteed.
史にf」利なのは、目的に沿った副産物ができて、この
副p1.物がl’f! =s的に利用できて、二次熱の
有効な利用かrjJ能なことである。What is beneficial to history is that by-products that meet the purpose are created, and this by-product p1. Things are l'f! It is possible to use secondary heat effectively.
第1図は半乾燥法に用いろセメントクリンカ焼成装置、
第2図は乾燥法に用いるセメントクリンカ焼成装置を示
す。
図中符号
l・・・ロータリーキルン、2・・予熱器、3・・・煙
道ガス取出し位置、4・・・噴射水反応器、5・・・捕
集容器、6・・純ガス排出管、7・・・支持換気扇、8
・・・煙道ガス換気扇、9・・・電子フィルタ、lO・
・・スラッジ分離器、1!・・スラッジ、12・・噴射
水反射器の運転用ポンプ、13・・・送り・戻し4管、
14゜I7・・・熱交換器、15・・フロート弁、16
・・・液体サイクロンの冷却装置、!8 ・浄化管用ポ
ンプ、19・・・蘂品11を給蒸、20・・洗浄水導管
、21・・・純ガス配管、22・・予熱器煙道ガス管、
23・・・煙道ガス混合物管、24・・純ガス排出1」
、25・・浄化管。Figure 1 shows the cement clinker firing equipment used in the semi-drying method.
Figure 2 shows a cement clinker firing device used in the drying method. Reference numeral l in the figure: Rotary kiln, 2: Preheater, 3: Flue gas extraction position, 4: Injection water reactor, 5: Collection container, 6: Pure gas discharge pipe, 7...Support ventilation fan, 8
... Flue gas ventilation fan, 9... Electronic filter, lO.
...Sludge separator, 1! ...Sludge, 12.. Pump for operating the jet water reflector, 13.. 4 feed/return pipes,
14゜I7...Heat exchanger, 15...Float valve, 16
...Liquid cyclone cooling device! 8 - Pump for purification pipes, 19... Steam supply for the equipment 11, 20... Cleaning water conduit, 21... Pure gas piping, 22... Preheater flue gas pipe,
23... Flue gas mixture pipe, 24... Pure gas discharge 1.
, 25...purification pipe.
Claims (1)
される、アルカリの少ないセメントクリンカを製造する
ための装置において、予熱器(2)とロータリーキルン
(1)との間の煙道ガス取出し位置(3)に噴射水反応
器(4)を配設してあることを特徴とする、装置。 2)煙道ガス取出し位置(3)の向かい側の噴射水反応
器(4)端部に捕集容器(5)を接続してあり、この捕
集容器が新水供給用フロート弁(15)、薬品供給装置
(19)、純ガス排出管(6)を有する、特許請求の範
囲1)に記載の装置。 3)純ガス排出管(6)から支持換気扇(7)が組み込
まれた純ガス配管(21)が予熱器煙道ガス管(22)
中に通しており、純ガス配管(21)は支持換気扇(7
)の後方に大気に至る純ガス排出口(24)を有し、純
ガス導管(23)中には電子フィルタ(9)に至る煙道
ガス換気扇(8)を敷設してある、特許請求の範囲1)
に記載の装置。 4)送り・戻し導管(13)を有する熱交換器(14)
を併設してある捕集容器(5)にポンプ(18)を有す
るスラッジ分離器(10)を後置接続してある、特許請
求の範囲1)または2)に記載の装置。[Claims] 1) A flue between the preheater (2) and the rotary kiln (1) in an apparatus for producing cement clinker with low alkali, which comprises a preheater, a rotary kiln, and a gas purification device. A device characterized in that a jet water reactor (4) is arranged at the gas extraction position (3). 2) A collection container (5) is connected to the end of the injection water reactor (4) opposite the flue gas extraction position (3), and this collection container is connected to a fresh water supply float valve (15), Device according to claim 1), comprising a drug supply device (19) and a pure gas discharge pipe (6). 3) Pure gas pipe (21) with built-in support ventilation fan (7) runs from pure gas discharge pipe (6) to preheater flue gas pipe (22)
The pure gas pipe (21) is connected to the supporting ventilation fan (7).
) has a pure gas outlet (24) leading to the atmosphere at the rear, and a flue gas ventilation fan (8) leading to an electronic filter (9) is installed in the pure gas conduit (23). Range 1)
The device described in. 4) Heat exchanger (14) with feed and return conduits (13)
2. The device according to claim 1, wherein a sludge separator (10) with a pump (18) is connected downstream to the collection vessel (5), which is associated with a sludge separator (10).
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DD84268386A DD234336A3 (en) | 1984-10-15 | 1984-10-15 | DEVICE FOR PRODUCING ALKALIUM CEMENT CLINKERS |
| DD04B/268386.1 | 1984-10-15 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPS61111948A true JPS61111948A (en) | 1986-05-30 |
Family
ID=5561352
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60227962A Pending JPS61111948A (en) | 1984-10-15 | 1985-10-15 | Apparatus for manufacturing cement clinker with small alkalicontent |
Country Status (11)
| Country | Link |
|---|---|
| JP (1) | JPS61111948A (en) |
| AT (1) | AT384803B (en) |
| CS (1) | CS269763B1 (en) |
| DD (1) | DD234336A3 (en) |
| DE (1) | DE3535721A1 (en) |
| DK (1) | DK467585A (en) |
| FI (1) | FI79088C (en) |
| NO (1) | NO853144L (en) |
| RO (1) | RO92947B (en) |
| SE (1) | SE8504755L (en) |
| SU (1) | SU1695115A1 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4708855A (en) * | 1985-11-07 | 1987-11-24 | Passanaquoddy Tribe | Method and system for exhaust gas stream scrubbing |
| US5100633A (en) * | 1985-11-07 | 1992-03-31 | Passamaquoddy Technology Limited Partnership | Method for scrubbing pollutants from an exhaust gas stream |
| US7984566B2 (en) * | 2003-10-27 | 2011-07-26 | Staples Wesley A | System and method employing turbofan jet engine for drying bulk materials |
-
1984
- 1984-10-15 DD DD84268386A patent/DD234336A3/en not_active IP Right Cessation
-
1985
- 1985-08-06 AT AT0230385A patent/AT384803B/en not_active IP Right Cessation
- 1985-08-08 NO NO853144A patent/NO853144L/en unknown
- 1985-10-07 DE DE19853535721 patent/DE3535721A1/en not_active Withdrawn
- 1985-10-08 SU SU857773970A patent/SU1695115A1/en active
- 1985-10-10 RO RO120338A patent/RO92947B/en unknown
- 1985-10-11 DK DK467585A patent/DK467585A/en not_active Application Discontinuation
- 1985-10-14 CS CS857300A patent/CS269763B1/en unknown
- 1985-10-14 SE SE8504755A patent/SE8504755L/en not_active Application Discontinuation
- 1985-10-15 JP JP60227962A patent/JPS61111948A/en active Pending
- 1985-10-15 FI FI854016A patent/FI79088C/en not_active IP Right Cessation
Also Published As
| Publication number | Publication date |
|---|---|
| SE8504755L (en) | 1986-04-16 |
| SE8504755D0 (en) | 1985-10-14 |
| FI854016A0 (en) | 1985-10-15 |
| DK467585D0 (en) | 1985-10-11 |
| CS730085A1 (en) | 1988-08-16 |
| AT384803B (en) | 1988-01-11 |
| RO92947A (en) | 1987-11-30 |
| FI854016L (en) | 1986-04-16 |
| DE3535721A1 (en) | 1986-04-30 |
| FI79088B (en) | 1989-07-31 |
| SU1695115A1 (en) | 1991-11-30 |
| DD234336A3 (en) | 1986-04-02 |
| DK467585A (en) | 1986-04-16 |
| ATA230385A (en) | 1987-06-15 |
| FI79088C (en) | 1989-11-10 |
| NO853144L (en) | 1986-04-16 |
| CS269763B1 (en) | 1990-05-14 |
| RO92947B (en) | 1987-12-01 |
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