TWI819065B - Combustible material processing methods and processing devices - Google Patents
Combustible material processing methods and processing devices Download PDFInfo
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- 239000000463 material Substances 0.000 title claims abstract description 34
- 238000003672 processing method Methods 0.000 title 1
- 239000002994 raw material Substances 0.000 claims abstract description 66
- 239000004568 cement Substances 0.000 claims abstract description 56
- 238000002156 mixing Methods 0.000 claims abstract description 37
- 238000002309 gasification Methods 0.000 claims abstract description 24
- 238000001354 calcination Methods 0.000 claims abstract description 21
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 21
- 238000006243 chemical reaction Methods 0.000 claims abstract description 14
- 239000007789 gas Substances 0.000 claims description 24
- 238000000034 method Methods 0.000 claims description 7
- 239000001301 oxygen Substances 0.000 claims description 6
- 229910052760 oxygen Inorganic materials 0.000 claims description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 5
- 239000000203 mixture Substances 0.000 claims description 2
- 238000002485 combustion reaction Methods 0.000 abstract description 18
- 239000002699 waste material Substances 0.000 abstract description 13
- 239000010849 combustible waste Substances 0.000 abstract description 12
- 239000004033 plastic Substances 0.000 abstract description 11
- 229920003023 plastic Polymers 0.000 abstract description 11
- 239000000571 coke Substances 0.000 abstract description 9
- 239000010802 sludge Substances 0.000 abstract description 8
- 239000002803 fossil fuel Substances 0.000 abstract description 7
- -1 chaff Substances 0.000 abstract description 5
- 239000010920 waste tyre Substances 0.000 abstract description 5
- 239000002023 wood Substances 0.000 abstract description 5
- 239000003638 chemical reducing agent Substances 0.000 description 14
- 239000003245 coal Substances 0.000 description 10
- 239000000446 fuel Substances 0.000 description 6
- 239000000567 combustion gas Substances 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 4
- 239000004202 carbamide Substances 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 238000004880 explosion Methods 0.000 description 4
- 239000000843 powder Substances 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 238000006114 decarboxylation reaction Methods 0.000 description 2
- 238000003913 materials processing Methods 0.000 description 2
- 239000010813 municipal solid waste Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000002253 acid Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000004069 differentiation Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 230000008676 import Effects 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- JTJMJGYZQZDUJJ-UHFFFAOYSA-N phencyclidine Chemical class C1CCCCN1C1(C=2C=CC=CC=2)CCCCC1 JTJMJGYZQZDUJJ-UHFFFAOYSA-N 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
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Abstract
[課題]一面維持穩定運轉,一面有效利用廢塑膠、廢輪胎、穀殼、木屑、PKS、RDF、汙泥等可燃性廢棄物,並且使石炭、焦炭等化石燃料的燃燒效率提升,進而更加減少水泥窯廢氣中的NOx濃度。 [解決手段]一種可燃物的處理裝置,具備:混合裝置,將可燃物與從水泥燒成裝置的預熱器旋風分離器分化出的600℃以上且900℃以下的預熱原料混合而氣化;及供給裝置,將氣化後的可燃物及預熱原料(混合原料)從水泥燒成裝置的窯尾供給至煅燒爐的區域。也可在將可燃物與預熱原料混合時添加水分而進行水煤氣化反應,並將產生出的水煤氣及預熱原料從水泥燒成裝置的窯尾導入煅燒爐的區域。[Problem] While maintaining stable operation, effectively utilize combustible waste such as waste plastics, waste tires, chaff, wood chips, PKS, RDF, and sludge, and improve the combustion efficiency of fossil fuels such as coke and coke, thereby further reducing NOx concentration in cement kiln exhaust gas. [Solution] A combustible material processing device equipped with a mixing device for mixing and gasifying the combustible material with preheated raw materials of 600°C or more and 900°C or less separated from the preheater cyclone of the cement burning device. ; and a supply device that supplies the gasified combustibles and preheated raw materials (mixed raw materials) from the kiln end of the cement burning device to the calcining furnace area. It is also possible to add water when mixing combustibles and preheated raw materials to perform a water gasification reaction, and introduce the generated water gas and preheated raw materials from the kiln end of the cement burning device into the calcining furnace area.
Description
本發明是有關於一種有效利用廢塑膠、廢輪胎、穀殼、木屑、PKS、RDF、汙泥等可燃性廢棄物,並且使前述可燃性廢棄物及石炭、焦炭等化石燃料的燃燒效率提升,進而更加效率良好地減少水泥窯廢氣中的NOx濃度之技術。The invention relates to a method that effectively utilizes combustible wastes such as waste plastics, waste tires, chaff, wood chips, PKS, RDF, sludge, etc., and improves the combustion efficiency of the aforementioned combustible wastes and fossil fuels such as coke and coke. This is a technology that can more efficiently reduce the NOx concentration in cement kiln exhaust gas.
都市垃圾等一般廢棄物及汙泥等產業廢棄物是直接掩埋處理或在垃圾焚化場等焚化。焚化時產生出的焚化灰會送至最終處理場,但近年來難有最終處理場的新地點,因此最終處理場的剩餘容量正持續緊繃。於是,有在將廢塑膠或汙泥等可燃性廢棄物進行焚化或氣化處理來加以有效利用(例如專利文獻1)。又,雖然有使可燃性廢棄物在窯尾或煅燒爐燃燒的技術,但為了增加處理量,需要粉碎得細小,或需要將煅燒爐內的燃燒時間從1~3秒改造成5秒以上。General waste such as municipal garbage and industrial waste such as sludge are directly buried or incinerated in garbage incineration plants. The incineration ash generated during incineration is sent to a final disposal site. However, in recent years, it has been difficult to find new locations for final disposal sites, so the remaining capacity of final disposal sites continues to be tight. Therefore, combustible wastes such as waste plastics and sludge are effectively utilized by incineration or gasification (for example, Patent Document 1). In addition, although there is a technology for burning combustible waste at the end of a kiln or a calciner, in order to increase the processing capacity, it needs to be ground into fine particles, or the combustion time in the calciner needs to be changed from 1 to 3 seconds to more than 5 seconds.
又,近來廢塑膠的排出量正在增加,並且中國等已變得禁止廢塑膠輸入,因此國內外的廢塑膠處理的需求正在增大。又,中國、韓國正在加強排放到大氣中的廢氣的NOx管制。In addition, the discharge amount of waste plastics is increasing recently, and China and other countries have banned the import of waste plastics, so the demand for waste plastic processing at home and abroad is increasing. In addition, China and South Korea are strengthening the control of NOx emissions into the atmosphere.
另一方面,水泥窯的廢氣中,包含起因於燒成區的高溫域的NOx,在NOx的濃度高時,會投入尿素或氨等的脫硝劑,或是藉由在煅燒爐中透過燃燒所產生的還原作用來減少NOx濃度。但是,利用尿素作為脫硝劑的方法之中,因為尿素昂貴而造成運作成本高漲。又,只添加尿素時的脫硝效率低,而且也會有未與NOx反應的剩餘的氨直接朝系統外排出的疑慮。On the other hand, the exhaust gas from the cement kiln contains NOx caused by the high temperature range of the calcining zone. When the concentration of NOx is high, denitrifying agents such as urea and ammonia are added, or through combustion in the calcining furnace. The reduction effect produced reduces NOx concentration. However, in the method of using urea as a denitrification agent, the operating cost is high because urea is expensive. In addition, the denitrification efficiency is low when only urea is added, and there is a concern that the remaining ammonia that has not reacted with NOx is directly discharged out of the system.
在此,本申請人提出了以下技術:設置將燃料及燃燒用空氣吹入水泥窯的窯尾內的脫硝用燃燒器,在窯尾內的低氧區域中還原水泥窯廢氣中的NOx,並且可利用燃燒燃料來使水泥原料的脫羧效率也提升,且不拘煅燒爐的形式,一面維持良好的燒成狀態一面效率良好地減少水泥窯廢氣中的NOx濃度(參照專利文獻2)。Here, the applicant proposed the following technology: installing a denitration burner that blows fuel and combustion air into the kiln tail of the cement kiln, and reducing NOx in the cement kiln exhaust gas in the low-oxygen zone in the kiln tail. In addition, the decarboxylation efficiency of cement raw materials can be improved by using combustion fuel, and the NOx concentration in the cement kiln exhaust gas can be efficiently reduced while maintaining a good firing state regardless of the type of calciner (see Patent Document 2).
專利文獻 專利文獻1:日本特開2018-155484號公報 專利文獻2:日本國專利第6476165號公報patent documents Patent Document 1: Japanese Patent Application Publication No. 2018-155484 Patent Document 2: Japanese Patent No. 6476165
發明概要 發明欲解決之課題 將廢塑膠、廢輪胎、穀殼、木屑、PKS、RDF、汙泥等可燃性廢棄物氣化時,因為會產生焦油,而有著因附著或堵塞等而妨害穩定運轉的問題。又,無法否定因燃燒而造成爆炸等的危險性。Summary of the invention The problem to be solved by the invention When flammable wastes such as waste plastics, waste tires, chaff, wood chips, PKS, RDF, and sludge are gasified, tar will be generated, which may cause adhesion or clogging, which may hinder stable operation. Furthermore, the risk of explosion due to combustion cannot be denied.
另一方面,關於水泥窯廢氣的脫硝,記載於專利文獻2的石炭的二段燃燒之中,也有著NOx的還原劑不足造成脫硝效果不充分,並且在石炭的導入部有皮膜(coating)附著等的問題。On the other hand, regarding the denitration of cement kiln exhaust gas, in the two-stage combustion of pebbles described in
在此,本發明是鑑於上述習知技術之問題點而完成者,其目的在於一面維持穩定運轉,一面有效利用廢塑膠、廢輪胎、穀殼、木屑、PKS、RDF、汙泥等可燃性廢棄物,並且使石炭、焦炭等化石燃料的燃燒效率提升,進而更加減少水泥窯廢氣中的NOx濃度。Here, the present invention was completed in view of the above-mentioned problems of the conventional technology, and its purpose is to effectively utilize combustible waste such as waste plastics, waste tires, chaff, wood chips, PKS, RDF, and sludge while maintaining stable operation. It also improves the combustion efficiency of fossil fuels such as coke and coke, thereby further reducing the NOx concentration in cement kiln exhaust gas.
用以解決課題之手段 為了達成上述目的,本發明是一種可燃物的處理方法,其特徵在於:將可燃物與從水泥燒成裝置的預熱器旋風分離器(preheater cyclone)分化出的600℃以上且900℃以下的預熱原料混合而氣化,且將氣化後的可燃物及前述預熱原料從水泥燒成裝置的窯尾供給至煅燒爐的區域。means to solve problems In order to achieve the above object, the present invention is a method for treating combustible materials, which is characterized in that the combustible materials and 600°C or more and 900°C or less differentiated from a preheater cyclone of a cement burning device The preheated raw materials are mixed and gasified, and the gasified combustibles and the preheated raw materials are supplied from the kiln tail of the cement burning device to the area of the calcining furnace.
依據本發明,藉由將可燃性廢棄物或化石燃料等可燃物與預熱原料混合,可避免氣化時產生出的焦油所造成的附著問題等。又,可藉由在無氧狀態下將可燃物氣化來使還原物質產生,且預熱原料中的Fe2 O3 也可還原成FeO而可增加還原劑的量。此外,可藉由氣化來縮短燃燒時間,因此即使是煅燒爐內的廢氣的滯留時間為1~3秒的習知的石炭燃燒用煅燒爐也可使可燃性廢棄物有效地燃燒,且可削減石炭使用量及產生的CO的量。包含還原劑的前述預熱原料伴隨包含還原劑的氣化後的可燃物從窯尾供給至煅燒爐的區域,可使粉體及氣體分散於氣體中,且可有效地還原水泥窯燃燒氣體中的NOx。此外,由於氣化後的可燃物及前述預熱原料導入煅燒爐,因此可避免皮膜的附著問題。又,由於可藉由氣化來縮短燃燒時間,因此亦可減少可燃物的粉碎電力。According to the present invention, by mixing combustible materials such as combustible waste or fossil fuels with preheated raw materials, adhesion problems caused by tar generated during gasification can be avoided. In addition, reducing substances can be generated by gasifying combustibles in an oxygen-free state, and Fe 2 O 3 in the preheated raw material can also be reduced to FeO, thereby increasing the amount of reducing agent. In addition, the combustion time can be shortened by gasification, so even a conventional calciner for pebble combustion in which the residence time of the exhaust gas in the calciner is 1 to 3 seconds can effectively burn combustible waste, and can Reduce the amount of coal used and the amount of CO generated. The aforementioned preheated raw material containing the reducing agent is supplied from the end of the kiln to the calcining furnace area along with the gasified combustibles containing the reducing agent, which can disperse the powder and gas in the gas and effectively reduce the cement kiln combustion gas. of NOx. In addition, since the gasified combustibles and the aforementioned preheated raw materials are introduced into the calcining furnace, the problem of film adhesion can be avoided. In addition, since the combustion time can be shortened by gasification, the power required for crushing combustibles can also be reduced.
前述可燃物的處理方法之中,可在將前述可燃物與前述預熱原料混合時添加水分而進行水煤氣化反應,並將產生出的水煤氣及前述預熱原料從水泥燒成裝置的窯尾導入煅燒爐的區域。由於是在未導入氧氣的情況下以水蒸氣來封住,因此沒有爆炸的危險性,且藉由水煤氣化反應產生H2 還原劑,並且原料中的Fe2 O3 也會還原成FeO,因此還原劑的量會跳躍性地增加。藉此,可有效地還原水泥窯燃燒氣體中的NOx。In the above method for treating combustibles, water can be added when the combustibles are mixed with the preheated raw materials to perform a water gasification reaction, and the generated water gas and the preheated raw materials can be introduced from the kiln end of the cement burning device. Calcining furnace area. Since it is sealed with water vapor without introducing oxygen, there is no risk of explosion, and the H 2 reducing agent is generated through the water gasification reaction, and the Fe 2 O 3 in the raw material will also be reduced to FeO, so The amount of reducing agent will increase dramatically. In this way, NOx in the cement kiln combustion gas can be effectively reduced.
又,本發明是一種可燃物的處理裝置,其特徵在於具備:混合裝置,將可燃物與從水泥燒成裝置的預熱器旋風分離器分化出的600℃以上且900℃以下的預熱原料混合而氣化;及供給裝置,將氣化後的可燃物及前述預熱原料從水泥燒成裝置的窯尾供給至煅燒爐的區域。Furthermore, the present invention is a combustible material processing device, characterized in that it is provided with a mixing device for mixing the combustible material and the preheated raw material of 600°C or more and 900°C or less separated from the preheater cyclone of the cement burning device. Mix and gasify; and a supply device supplies the gasified combustibles and the aforementioned preheated raw materials from the kiln tail of the cement burning device to the calcining furnace area.
依據本發明,藉由將可燃性廢棄物或化石燃料等可燃物與預熱原料混合,可避免氣化時產生出的焦油所造成的附著問題等。又,可藉由在無氧狀態下將可燃物氣化來使還原物質產生,且預熱原料中的Fe2 O3 也可還原成FeO而可增加還原劑的量。此外,可藉由氣化來縮短燃燒時間,因此即使是煅燒爐內的廢氣的滯留時間為1~3秒的習知的石炭燃燒用煅燒爐也可使可燃性廢棄物有效地燃燒,且可削減石炭使用量及產生的CO的量。包含還原劑的前述預熱原料伴隨包含還原劑的氣化後的可燃物從窯尾供給至煅燒爐的區域,可使粉體及氣體分散於氣體中,且可有效地還原水泥窯燃燒氣體中的NOx。此外,由於氣化後的可燃物及前述預熱原料導入煅燒爐,因此可避免皮膜的附著問題。又,由於可藉由氣化來縮短燃燒時間,因此亦可減少可燃物的粉碎電力。According to the present invention, by mixing combustible materials such as combustible waste or fossil fuels with preheated raw materials, adhesion problems caused by tar generated during gasification can be avoided. In addition, reducing substances can be generated by gasifying combustibles in an oxygen-free state, and Fe 2 O 3 in the preheated raw material can also be reduced to FeO, thereby increasing the amount of reducing agent. In addition, the combustion time can be shortened by gasification, so even a conventional calciner for pebble combustion in which the residence time of the exhaust gas in the calciner is 1 to 3 seconds can effectively burn combustible waste, and can Reduce the amount of coal used and the amount of CO generated. The aforementioned preheated raw material containing the reducing agent is supplied from the end of the kiln to the calcining furnace area along with the gasified combustibles containing the reducing agent, which can disperse the powder and gas in the gas and effectively reduce the cement kiln combustion gas. of NOx. In addition, since the gasified combustibles and the aforementioned preheated raw materials are introduced into the calcining furnace, the problem of film adhesion can be avoided. In addition, since the combustion time can be shortened by gasification, the power required for crushing combustibles can also be reduced.
前述可燃物的處理裝置之中,可具備:水分添加裝置,在前述混合裝置中添加水分而使水煤氣化反應進行。藉此,可消除爆炸的危險性,且藉由水煤氣化反應產生H2 還原劑,原料中的Fe2 O3 也會還原成FeO,因此還原劑的量會跳躍性地增加,而有效地還原水泥窯燃燒氣體中的NOx。又,水煤氣化反應是吸熱反應,基本上也不會有溫度過於上升的狀況,因此可用SUS310S作為混合裝置的材料。假設即使溫度上升,也會藉由水分的蒸發、原料的脫羧來進行吸熱,最高也只會溫度上升至850℃。 發明效果The above-mentioned combustible material processing device may include a moisture adding device, and the moisture is added to the mixing device to cause the water-coal gasification reaction to proceed. In this way, the risk of explosion can be eliminated, and the H 2 reducing agent is generated through the water-coal gasification reaction. Fe 2 O 3 in the raw material will also be reduced to FeO, so the amount of reducing agent will increase dramatically, effectively reducing NOx in cement kiln combustion gas. In addition, the water-gasification reaction is an endothermic reaction, and there is basically no excessive temperature rise. Therefore, SUS310S can be used as the material of the mixing device. Assuming that even if the temperature rises, heat will be absorbed through evaporation of water and decarboxylation of raw materials, and the temperature will only rise to a maximum of 850°C. Invention effect
如上所述,依據本發明,可一面維持穩定運轉,一面有效利用廢塑膠或汙泥等可燃性廢棄物,並且使石炭、焦炭等化石燃料的燃燒效率提升,進而更加減少水泥窯廢氣中的NOx濃度。As described above, according to the present invention, while maintaining stable operation, it is possible to effectively utilize combustible wastes such as waste plastics and sludge, and improve the combustion efficiency of fossil fuels such as coke and coke, thereby further reducing NOx in the cement kiln exhaust gas. concentration.
圖1顯示本發明之可燃物的處理裝置之一實施形態,該處理裝置1具備:加料漏斗2,容受可燃物C;混合裝置3,將從加料漏斗2供給的可燃物C與從水泥燒成裝置10的預熱器11的下方算來第2段的旋風分離器11B分化出的600℃以上且900℃以下的預熱原料R2混合而氣化;及供給裝置5,將氣化後的可燃物C及預熱原料R2(也包含未氣化的可燃物C,以下稱為「混合原料M」)從水泥燒成裝置10的水泥窯13的窯尾13a供給至煅燒爐12的區域。另外,圖1中,雖然描繪了2個旋風分離器11B,但為了方便說明,2個都是相同之物。Figure 1 shows one embodiment of the combustible material processing device of the present invention. The
上述處理對象之可燃物C是廢塑膠、廢輪胎、穀殼、木屑、PKS、RDF、汙泥等可燃性廢棄物,或石炭、焦炭等化石燃料等。The above-mentioned combustible materials C are waste plastics, waste tires, chaff, wood chips, PKS, RDF, sludge and other combustible wastes, or fossil fuels such as pebbles and coke.
混合裝置3是在水平軸3a安裝有多數個葉片3b,藉由使水平軸3a旋轉,讓葉片3b也進行旋轉的混合機(pug mill)等,且將可燃物C與預熱原料R2混合而氣化。The
在混合裝置3的上方,設置有灑水裝置(不圖示),在混合裝置3內灑水(供給水分W),進行水煤氣化反應。為了防止因為急遽的水蒸氣產生而增加飛散灰塵,在混合裝置3設置有罩體(hood)3c。A water sprinkling device (not shown) is provided above the
在混合裝置3的下方,設置有關斷式擋板(shut-off damper)4,一面保有氣密性一面將混合原料M透過供給裝置5從水泥燒成裝置10的水泥窯13的窯尾13a導入煅燒爐12的區域。又,設置有將氣化後的氣體G排出的排氣導管6,從排氣導管6排出的氣體G在關斷式擋板4的下方與混合原料M會合,並透過供給裝置5從水泥燒成裝置10的水泥窯13的窯尾13a導入煅燒爐12的區域。供給裝置5中可利用斜槽(shoot)、導管、輸送機。A shut-
附設有上述處理裝置1的水泥燒成裝置10與習知的裝置相同,是由以下構件等所構成:預熱器11,將水泥原料R1預熱;煅燒爐12,將來自從預熱器11的下方算來第2段的旋風分離器11B的預熱原料R2煅燒;水泥窯13,藉由從主燃燒器15吹入的燃料F,將來自預熱器11的最下段的旋風分離器11A的原料R3燒成;及熟料冷卻器14,將水泥窯13中燒成出的水泥熟料冷卻。另外,較理想的是在供給裝置5的混合原料M的供給位置中,設置本案申請人的日本特許第6396433號公報的粉粒體分散裝置,使氣化後的可燃物C及粉體的預熱原料有效地分散在氣體中。The
其次,針對利用上述處理裝置1所進行的可燃物的處理方法,一面參照圖1一面進行說明。Next, a method of processing combustible materials using the above-mentioned
水泥燒成裝置10運轉時,將加料漏斗2中容受的可燃物C供給至混合裝置3,並且將從預熱器11的旋風分離器11B排出的預熱原料R2的一部份分化,且將分化出的預熱原料R2導入混合裝置3。另外,未被分化的預熱原料R2則如通常一樣在煅燒爐5、最下段的旋風分離器11A進行脫羧之後,會在水泥窯13進行燒成而生成水泥熟料。When the
在混合裝置3中,將可燃物C與預熱原料R2一面混合攪拌一面搬送,藉由分化出的預熱原料R2將可燃物C加熱而氣化,並且從灑水裝置灑水,進行水煤氣反應。藉由將可燃物C與預熱原料R2混合,可避免氣化時產生出的焦油所造成的附著問題。又,由可燃物C產生出的酸性氣體可固定於預熱原料R2。此外,可藉由氣化來縮短燃燒時間,因此即使是習知的石炭燃燒用的煅燒爐12也可有效地燃燒,且可削減石炭使用量及產生的CO的量。In the
另外,可燃物C與預熱原料R2的混合比率並未特別限定,但在可燃物C附著於混合裝置3的內部或搬送路徑時,會使預熱原料R2的混合比率增加。又,在處理廢塑膠等時,較理想的是在混合裝置3的前段事先粉碎至200mm以下左右。又,較理想的是將混合裝置3中的可燃物C的滯留時間設在5~15分,並將混合裝置3的水平軸3a的旋轉速度作成可變,且將滯留時間構成為可調整。In addition, the mixing ratio of the combustible material C and the preheated raw material R2 is not particularly limited. However, when the combustible material C adheres to the inside of the
又,由於是在未將氧氣導入混合裝置3的情況下以水蒸氣來封住,因此沒有爆炸的危險性,且藉由水煤氣化反應產生H2
還原劑,並且預熱原料R2中的Fe2
O3
也會還原成FeO,因此還原劑的量會跳躍性地增加。In addition, since oxygen is sealed with water vapor without introducing oxygen into the
從混合裝置3排出的混合原料M是經過關斷式擋板4,藉由供給裝置5從水泥燒成裝置10的水泥窯13的窯尾13a供給至煅燒爐12的區域。如上述,由於還原劑的量跳躍性地增加,因此可有效地還原水泥窯燃燒氣體中的NOx。又,混合原料M當中,未氣化的可燃物C是在煅燒爐12中作為代替燃料來利用,分化出的預熱原料R2在煅燒爐12、最下段的旋風分離器11A進行脫羧之後,會在水泥窯13進行燒成而生成水泥熟料。The mixed raw material M discharged from the
另外,在上述實施形態中,雖然是從預熱器11的旋風分離器11B分化出預熱原料R2,但只要分化的水泥原料的溫度在600℃以上且900℃以下的話,也可從其他部位分化。In addition, in the above-mentioned embodiment, although the preheating raw material R2 is differentiated from the cyclone 11B of the
又,雖然設置灑水裝置,在混合裝置3內灑水來進行水煤氣化反應,但即便不灑水,只由分化出的預熱原料R2來將可燃物C混合而氣化,也會有可避免氣化時產生出的焦油所造成的附著問題,且可藉由氣化來縮短燃燒時間等效果,還可一面維持處理裝置1及水泥燒成裝置10的穩定運轉,一面有效利用可燃物C,並且減少水泥窯廢氣中的NOx濃度。In addition, although a sprinkler device is provided to sprinkle water in the
此外,混合裝置3的構成並非限定成上述的構成,只要是可由分化出的預熱原料R2來將可燃物C混合而氣化,除此之外,還可添加水分而進行水煤氣化反應的話,也可採用其他種類的裝置。In addition, the structure of the
1:可燃物的處理裝置 2:加料漏斗 3:混合裝置 3a:水平軸 3b:葉片 3c:罩體 4:關斷式擋板 5:供給裝置 6:排氣導管 10:水泥燒成裝置 11:預熱器 11A:旋風分離器 11B:旋風分離器 12:煅燒爐 13:水泥窯 13a:窯尾 14:熟料冷卻器 15:主燃燒器 C:可燃物 F:燃料 G:氣體 M:混合原料 R1:水泥原料 R2:預熱原料 R3:原料 W:水分1: Combustible materials processing device 2: Adding funnel 3: Mixing device 3a: Horizontal axis 3b: blade 3c: Cover body 4: Shut-off baffle 5: Supply device 6:Exhaust duct 10: Cement burning device 11:Preheater 11A: Cyclone separator 11B: Cyclone separator 12:Calcining furnace 13:Cement kiln 13a: kiln end 14:Clinker cooler 15: Main burner C: Combustibles F:Fuel G: gas M: mixed raw materials R1: cement raw materials R2: Preheat raw materials R3: raw materials W:moisture
圖1是顯示本發明之可燃物的處理裝置之一實施形態的概略圖。FIG. 1 is a schematic diagram showing an embodiment of the combustible material processing apparatus of the present invention.
1:可燃物的處理裝置 1: Combustible materials processing device
2:加料漏斗 2: Adding funnel
3:混合裝置 3: Mixing device
3a:水平軸 3a: Horizontal axis
3b:葉片 3b: blade
3c:罩體 3c: Cover body
4:關斷式擋板 4: Shut-off baffle
5:供給裝置 5: Supply device
6:排氣導管 6:Exhaust duct
10:水泥燒成裝置 10: Cement burning device
11:預熱器 11: Preheater
11A:旋風分離器 11A: Cyclone separator
11B:旋風分離器 11B: Cyclone separator
12:煅燒爐 12:Calcining furnace
13:水泥窯 13:Cement kiln
13a:窯尾 13a: kiln end
14:熟料冷卻器 14:Clinker cooler
15:主燃燒器 15: Main burner
C:可燃物 C: Combustibles
F:燃料 F:Fuel
G:氣體 G: gas
M:混合原料 M: mixed raw materials
R1:水泥原料 R1: cement raw materials
R2:預熱原料 R2: Preheat raw materials
R3:原料 R3: raw materials
W:水分 W:moisture
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