TW508275B - Method for burning wastes almost without generating dioxin, inhibitor of generating dioxin, and Method of producing the inhibitor - Google Patents

Method for burning wastes almost without generating dioxin, inhibitor of generating dioxin, and Method of producing the inhibitor Download PDF

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TW508275B
TW508275B TW90112491A TW90112491A TW508275B TW 508275 B TW508275 B TW 508275B TW 90112491 A TW90112491 A TW 90112491A TW 90112491 A TW90112491 A TW 90112491A TW 508275 B TW508275 B TW 508275B
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Taiwan
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dioxin
waste
hydrogen chloride
chloride gas
powder
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TW90112491A
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Chinese (zh)
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Tetsuo Murakami
Masuzo Murakami
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Shiina Keiji
Zeolite Chemical Ind Inc
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Priority claimed from JP2000359970A external-priority patent/JP2001215007A/en
Application filed by Shiina Keiji, Zeolite Chemical Ind Inc filed Critical Shiina Keiji
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Publication of TW508275B publication Critical patent/TW508275B/en

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Abstract

The invention provides a technology to largely decrease generation of dioxin in combustion ashes as well as exhaust gas by use of an ordinary combustion apparatus. The invention spreads over wastes being burnt an inhibitor for inhibiting generation of dioxin that comprises as main contents an adsorbing substance superior in rate of adsorbing hydrogen chloride gas and a reaction substance superior in reactivity with hydrogen chloride gas, and additionally a degradation agent when required, those mixed, granulated and dried, whereby a powder material removes hydrogen chloride gas in combustion gas and flying ashes and a granular material removes hydrogen chloride gas in residual ashes, thereby inhibiting generation of dioxin.

Description

發明説明(l ) 發明背景 發明領域 本發明係關於一種幾乎不產生戴奧辛之廢棄物焚燒方 法,抑制戴奧辛產生之抑制劑,及製造此抑制劑之方法。 先行技藝 爲了減少在焚燒廢棄物時產生之戴奧辛,迄今已發展 各種抑制戴奧辛產生之抑制劑,如含氧化鈦之解析劑觸媒 ,及去除戴奧辛先質、或氯化氫之抑制劑,及各種使用抑 制劑之焚燒廢棄物技術。此外已發展一種氣化及溶解技術 ,其中利用戴奧辛在1000至1 500°C之非常高溫度焚燒時溶 解之事實,將來自燃燒槽或區中焚燒廢棄物之高溫燃燒氣 體之廢氣在1 000至1 500°C之溫度再焚燒。 習知戴奧辛去除技術目標主要爲去除或減少來自高溫燃 燒氣體之廢氣所含之戴奧辛。以上之習知抑制劑抑制戴奧 辛產生,而且溶解-焚燒(氣化/溶解)技術具有去除或減少 廢氣中戴奧辛之效果。關於此點,迄今已提議許多嚐試: 藉由將碳酸鉀加入鍋爐與集塵器間之低氧大氣中之去氯反 應(日本未審查專利申請案Hei 1 1 - 9959 ( 1 999 ));將來自 焚化爐之燃燒氣體之廢氣冷卻至220至230°C且接受氫氧 化鈣與活性碳噴灑,使得氫氧化鈣中和酸性氣體及活性碳 吸收戴奧辛與汞(日本未審查專利申請案He 1 7 - 20443 2 ( 1 995 ));在處理過程時低於400°C之前之處以戴奧辛先 質之吸附/去除材料應用於廢氣(利用在超過400°C不易製 造而在200至400°C容易製造戴奧辛之事實)(日本未審查 508275 五、發明説明(2 ) 專利申請案He 1 9 - 220438( 1 997 ));吸附戴奧辛及自廢氣 去除(日本未審查專利申請案Hei 1 0 - 1 28062( 1 998 ));在 焚化爐之煙道上吹送戴奧辛吸附劑,如酸黏土(日本未審 查專利申請案He! 1 1 - 9963 ( 1 999 ));藉由使用含鈦之觸 媒溶解廢氣中之戴奧辛及其他之技術或方法(日本未審查 專利申請案 Hei 2 - 3591 4( 1 990 ) ;Hei 3- 841 5 ( 1 99 1 );DESCRIPTION OF THE INVENTION (1) Background of the Invention Field of the Invention The present invention relates to a waste incineration method that hardly produces dioxin, an inhibitor that inhibits dioxin production, and a method for manufacturing the inhibitor. In order to reduce the dioxin produced during the incineration of waste, various inhibitors that inhibit the production of dioxin, such as catalysts containing titanium oxide, as well as inhibitors for removing the dioxin precursor or hydrogen chloride, have been developed so far. Technology for incineration of waste. In addition, a gasification and dissolution technology has been developed, which utilizes the fact that dioxin dissolves when incinerated at a very high temperature of 1000 to 1,500 ° C, and the exhaust gas from the high-temperature combustion gas of incineration waste in the combustion tank or zone is in the range of 1 000 to Re-burn at a temperature of 1 500 ° C. The goal of conventional dioxin removal technology is to remove or reduce dioxin contained in exhaust gas from high-temperature combustion gases. The above-mentioned conventional inhibitors inhibit the production of dioxin, and the dissolution-incineration (gasification / dissolution) technology has the effect of removing or reducing dioxin in exhaust gas. In this regard, many attempts have been proposed so far: Dechlorination by adding potassium carbonate to a low-oxygen atmosphere between the boiler and the dust collector (Japanese unexamined patent application Hei 1 1-9959 (1 999)); future The exhaust gas of the combustion gas of the self-incinerator is cooled to 220 to 230 ° C and sprayed with calcium hydroxide and activated carbon, so that calcium hydroxide neutralizes acid gases and activated carbon to absorb dioxin and mercury (Japanese unexamined patent application He 1 7 -20443 2 (1 995)); use Dioxin pre-adsorption / removal material for exhaust gas before the treatment process is lower than 400 ° C (using difficult to manufacture at more than 400 ° C and easy to manufacture at 200 to 400 ° C Facts of dioxin) (Japanese unexamined 508275 V. Description of invention (2) Patent application He 1 9-220438 (1 997)); Adsorption of dioxin and removal from exhaust gas (Japanese unexamined patent application Hei 1 0-1 28062 ( 1 998)); blowing dioxin adsorbents such as acid clay on the flue of the incinerator (Japanese Unexamined Patent Application He! 1 1-9963 (1 999)); dissolving the Dioxin and other technologies or methods (Japanese Unexamined Patent Application Hei 2 - 3591 4 (1 990); Hei 3- 841 5 (1 99 1);

Hei 4-265122(1992)等)。 然而,利用氧化鈦作爲主要材料之習知戴奧辛產生抑 制劑製造昂貴且需要經常應用,因而整體上花費高成本。 而且基於溶解-焚燒技術之裝置(氣化/溶解烤箱)對廢棄 物比一般焚化爐貴約1 0倍,及難以縮小,使得其無法廣 爲流傳。氣化/溶解烤箱不可避免地需要連續地處置大量 廢棄物,其具有由各處廣泛地連接及運輸廢棄物之問題, 而且關於此點需得到接近運輸路線之住戶諒解。 此外,這些方法確實實質上無法去除來自焚燒廢棄物 之灰(殘餘灰)中之戴奧辛。來自焚燒廢棄物之灰僅以混 合將固化之設定劑(例如,水泥)及埋於地下之方式處置 。近來,在成本不爲問題之情形幾乎完成去除來自高溫 燃燒氣體之廢氣中之戴奧辛。但是全世界處置及焚燒大 量之廢棄物。以低成本無限地防止來自焚燒廢棄物之大 氣排放之戴奧辛產生爲相當嚴重及重要之課題。除了以 上將固化灰埋在地下之方法,說是完全沒有任何去除來 自焚燒廢棄物之灰中之戴奧辛之解決方法並不誇大。 發明人已精細地硏究以解決這些缺點,而且成功地發 -4- 508275 五、發明説明(3 ) 展以相當低之成本防止排放在大氣中之戴奧辛產生之焚 燒廢棄物,及幾乎完全地去除來自焚燒廢棄物之灰中之 戴奧辛之獨特方法,及用於此獨特廢棄物焚燒方法之戴 奧辛產生抑制劑。 發明槪要 本發明係關於一種具有相當少之戴奧辛產生之焚燒廢 棄物方法,最適合實行此廢棄物焚燒方法之戴奧辛產生 抑制劑,及製造此種抑制劑之方法。 本發明亦關於一種製造RDF之方法,其具有相當少之 氯化氫氣體與戴奧辛產生。 依照本發明之戴奧辛產生抑制劑包括粒狀或粉狀材料 或其混合物,其包括吸附氯化氫氣體速率優異之吸附物 質作爲主要內容物,及與氯化氫氣體之反應性優異之反 應物質。抑制劑散佈於被焚燒之廢棄物以去除燃燒氣體 ’飛灰與殘餘灰中之氯化氫氣體,因而抑制戴奧辛產生。 第1圖爲顯示用於小工廠之小型焚化爐之側視圖。 第2圖爲顯示在第1圖中之小型焚化爐中組合之散射裝 置之平面圖。 第3圖爲顯示安裝散射裝置之大型焚化爐之主要部份 之切面圖。 第4圖爲顯示依照本發明之戴奧辛產生抑制劑之結構 之略示圖。 發明詳細說明 本發明快速地及確實地去除在焚燒廢棄物時產生鹵素 508275 五、發明説明(4 ) 化合物(以下稱爲π氯化氫氣體",而且爲戴奧辛產生來 源),如氯化氫氣體與氯化溴氣體,以防止戴奧辛產生。 戴奧辛包括苯環、氯(溴)及氧,而且在重金屬及200 至600°C之熱存在下,由廢棄物中之氯化物與有機物質間 之化學反應製造。已知氯化氫氣體反應氧化鈣(生石灰) 或氫氧化鈣(熟石灰)變成氯化鈣。因此,大部份之習知 戴奧辛產生抑制劑由生石灰與熟石灰製成,及花費長反 應時間且無法充分地捕獲連續發生之氯化氫氣體。 發明人認爲在此情形下,生石灰或熟石灰與吸附物質 之組合快速地且確實地捕捉及捕獲在焚燒氣體時連續產 生之氯化氫氣體,並且完成本發明。因此,發明人發展 各種吸附氯化氫氣體速率優良之吸附物質,亦及應用於 被焚燒廢棄物之戴奧辛產生抑制劑之形狀與應用方法。 以下詳述本發明。如上,依照本發明戴奧辛產生抑制 劑確實包括快速地且確實地捕捉及捕獲氯化氫氣體之吸 附物質、及與氯化氫氣體而保有氯之反應物質,作爲主 要內容物。反應物質可使用氧化鈣(生石灰)或氫氧化鈣 (熟石灰),或其混合物。形成顆粒之依照本發明之戴奧 辛產生抑制劑中大部份之反應物質使用熟石灰。 吸附物質爲吸附速率優異之材料較佳。表1顯示各種物 質之吸附速率。測量操作以將0 . 5克之各樣本各置於各具 有3000毫升容量與瓶塞之聚丙烯容器中,繼而將2毫升之 99 . 99 9%氯化氫氣體應用至各容器且蓋上瓶塞及靜置之方 式進行。容器中之氯化氫氣體濃度在蓋上瓶塞後立即、應 508275 五、發明説明(5 ) 用氯化氫氣體後1 0分鐘、及此應用後20分鐘之時間,使 用Kitgawa指示劑管測量(由:Himec有限公司、Chugoku 區辦公室測量)。表1中低於0 . 1之起初濃度表示此例中全 部吸附30ppm氯化氫氣體之事實。 表1 樣本 氯化氬氣體濃度(ppm) 起初 10分鐘後 2 0分鐘後 空白 30 30 30 咖啡粉 10 4 低於0 . 1 活化咖啡粉 低於0 . 1 低於0 . 1 低於0 . 1 飛灰 3 0.3 低於0 . 1 活化飛灰 低於0 . 1 低於0 . 1 低於0 . 1 ΐ吏用過之茶葉 低於0 . 1 低於0 . 1 低於0 . 1 活性碳 5 2 低於0 . 1 WWm 17 8 低於0 . 1 白雲石 12 12 低於0 . 1 合成沸石 1 4 0.4 低於0. 1 合成沸石 1 低於0 . 1 低於0 . 1 低於0 . 1 本發明認爲吸附物質之吸附速率爲重要的之原因如下。 詳細言之,視焚化爐之規模而定,燃燒氣體變成然後經煙 函排放至大氣之廢氣化費約5至10秒或略有差異。在此過 程期間,氣體反應有機物質製造戴奧辛。因此,在吸附 氯化氫氣體花費1分鐘之情形,此時產生戴奧辛,而且將 殘餘氯化氫氣體排放至大氣。 其次解釋表1中顯示起初濃度低於0 . 1者。由於吸附物 質細微且漂浮性優異,活化咖啡粉爲已提供咖啡,而且具 有約50%水含量及在100至140°c乾燥且在100篩目下,更 佳爲在200篩目下,更佳爲在300篩目下粉碎之使用過咖 啡材料。亦由於咖啡粉在具有低水含量時更易粉碎,較佳 -7- 508275 五'發明説明(6 ) 爲將其乾燥成具有2%或更低之水含量。由於在lOOt或更 低乾燥花費長時間,而且在140°C乾燥造成咖啡粉在表面上 滲油及吸附氯化氫氣體之能力變差,乾燥較佳爲在120至 13 0°C,更佳爲約125t進行。僅乾燥至5至10%水含量之 使用過咖啡粉之吸附速率比活性碳不良。以如咖啡粉之相 同方式將使用過茶葉乾燥及硏磨,而且吸附力比咖啡粉僅 稍差,使得使用過茶葉需要以稍大之量應用。此外,在咖 啡粉與石灰應用(約5至1 0重量% )或具有5至1 0%水含量 時,可有效地容易地有利地硏磨。 飛灰爲由火力發電廠等大量排放者,而且pH爲3至13, 視使用之煤的種類及火力發電廠之特定設備而定,因而 具有或顯示不同之吸附氯化氫氣體之吸附速率。表1之 飛灰顯示藉由混合具有不同pH値之各種飛灰而具有pH 10 (及CEC(陽離子交換力)最大約120)之飛灰吸附力。因此 ,表1之飛灰難以實際使用。對於本發明,較佳爲使用活 化自由選擇之飛灰提供之活化飛灰。飛灰之活化涉及混 合飛灰與熟石灰,將水加入且攪拌及靜置2至3小時。飛 灰與熟石灰之混合比例可自行判斷,但是飛灰之比例較 佳爲超過熟石灰,例如,60至80重量%之飛灰及20至40 重量%之熟石灰。然後將混合物中之沈澱乾燥及在1 00至 2 00篩目下,更佳爲在300篩目下粉碎,以得到顯示pH 12 至13及CEC 150至200,而且吸附氯化氫氣體速率相當高 之優良吸附物質。 其次詳述合成沸石。用於合成淸潔劑等之一般合成沸 508275 五、發明説明(7 ) 石(表1之合成沸石1 )具有僅比活性碳高一點之吸附速率 ,因此對本發明不佳。另一種沸石,合成沸石2( Tosoh 公司以商標名"Ze ο 1 um "提供)顯示等於活化咖啡粉及活化 飛灰之吸附速率。"Zeolum"吸附硫化氫、二氧化硫或其 他氣體亦如氯化氫氣體優異,但是由於高成本而成問題。 如椰子殼、榨大豆、及白雲石之其他材料在氣體應用 2 0分鐘後顯示低於〇 . 1之氯化氫氣體濃度,但是無法用 於需要快速吸附之本發明。表1所示以外之顯示或具有如 活化咖啡粉與活化飛灰之相同或同等吸附速率之任何其 他吸附材料可完全應用於本發明,其條件爲其可較佳地 以低成本得到。米殼在碳化時顯示相當高之吸附速率, 但是碳化麻煩且耗時。在有效之碳化方法可得時,米殼 可用於本發明。此外,來自大量製造之農業產物之廢棄 物,如麥殼或榨甘蔗,可嚐試作爲得到顯示高吸附速率 及處置廢棄物方面方便性之材料之特定處理。 依照本發明之戴奧辛產生抑制劑立即或快速地吸附及 保持在焚燒廢棄物時產生之氯化氫氣體,然後造成氯化 氫氣體反應熟石灰及/或生石灰而消滅。關於此點,較佳 爲使用任何對氯化氫氣體具有優良反應效率之材料作爲 鈣化合物。 依照本發明之戴奧辛產生抑制劑以50至85重量%之鈣 化合物(熟石灰、生石灰等)混合50至1 5重量%之吸附物 質’繼而將適量之水加入混合物且粒化及乾燥之方式提 供。更佳之混合比例爲的65至75重量%之鈣化合物與約35 508275 五、發明説明(8 )Hei 4-265122 (1992), etc.). However, the conventional dioxin, which uses titanium oxide as a main material, produces inhibitors that are expensive to manufacture and require frequent application, and therefore cost high as a whole. In addition, the dissolution-incineration technology-based device (gasification / dissolution oven) is about 10 times more expensive than ordinary incinerators, and difficult to shrink, making it impossible to spread widely. The gasification / dissolving oven inevitably requires the continuous disposal of a large amount of waste, which has the problem of extensively connecting and transporting waste from various places, and this point needs to be understood by residents close to the transportation route. In addition, these methods do not substantially remove dioxin from the ash (residual ash) from incineration waste. Ash from incineration waste should only be disposed of by mixing solidified setting agents (eg, cement) and buried underground. Recently, dioxin has been almost completely removed from the exhaust gas from the high-temperature combustion gas without the cost being a problem. However, large amounts of waste are disposed of and incinerated worldwide. It is a very serious and important issue to prevent the generation of dioxin at low cost and infinitely prevent the atmospheric emission from waste incineration. Except for the above method of burying solidified ash in the ground, there is no solution to remove dioxin from the ash from incineration waste at all. It is not exaggerated. The inventors have meticulously researched to solve these shortcomings, and have succeeded in developing -4-508275 V. Description of the Invention (3) The development of dioxin incineration at a relatively low cost is prevented, and almost completely A unique method for removing dioxin from the ashes from incineration waste, and a dioxin production inhibitor for this unique waste incineration method. SUMMARY OF THE INVENTION The present invention relates to a method of incineration waste having relatively little dioxin generation, a dioxin generation inhibitor most suitable for implementing the waste incineration method, and a method for manufacturing such an inhibitor. The present invention also relates to a method for manufacturing RDF, which has a relatively small amount of hydrogen chloride gas and dioxin produced. The dioxin production inhibitor according to the present invention includes a granular or powdery material or a mixture thereof, which includes an adsorbed substance having an excellent rate of adsorbing hydrogen chloride gas as a main content, and a reaction substance having an excellent reactivity with hydrogen chloride gas. The inhibitor is dispersed in the incinerated waste to remove the combustion gas, the hydrogen chloride gas in the fly ash and the residual ash, thereby inhibiting the production of dioxin. Figure 1 is a side view showing a small incinerator for a small plant. Fig. 2 is a plan view showing a scattering device combined in the small incinerator of Fig. 1; Fig. 3 is a sectional view showing a main part of a large-scale incinerator in which a scattering device is installed. Fig. 4 is a schematic diagram showing the structure of a dioxin production inhibitor according to the present invention. Detailed description of the invention The present invention quickly and surely removes halogens generated during the incineration of waste 508275 5. Description of the invention (4) Compounds (hereinafter referred to as π hydrogen chloride gas " and sources of dioxin generation), such as hydrogen chloride gas and chlorination Bromine gas to prevent dioxin production. Dioxin includes benzene ring, chlorine (bromine), and oxygen, and is produced by chemical reaction between chlorides and organic substances in waste in the presence of heavy metals and heat at 200 to 600 ° C. It is known that hydrogen chloride gas reacts with calcium oxide (fast lime) or calcium hydroxide (hydrated lime) to become calcium chloride. Therefore, most of the conventional dioxin production inhibitors are made of quicklime and slaked lime, and it takes a long reaction time and cannot sufficiently capture continuously occurring hydrogen chloride gas. The inventors believe that in this case, quick limes or a combination of slaked lime and an adsorbent quickly and surely capture and capture the hydrogen chloride gas continuously generated during the incineration of the gas, and completed the present invention. Therefore, the inventors have developed various adsorption substances having excellent adsorption rate of hydrogen chloride gas, as well as the shape and application method of dioxin production inhibitor applied to incinerated waste. The present invention is described in detail below. As described above, the dioxin production inhibitor according to the present invention does include, as main contents, an adsorbing substance that rapidly and surely captures and captures hydrogen chloride gas and a reactive substance that retains chlorine with the hydrogen chloride gas. The reaction substance may be calcium oxide (fast lime) or calcium hydroxide (slaked lime), or a mixture thereof. Granulated lime is used for most of the reactive substances in the dioxin production inhibitors according to the present invention that form granules. The adsorption substance is preferably a material having an excellent adsorption rate. Table 1 shows the adsorption rates of various substances. The measurement operation was to place each sample of 0.5 g in a polypropylene container each having a capacity of 3000 ml and a stopper, and then apply 2 ml of 99.99 9% hydrogen chloride gas to each container and cap the stopper and stand still. Way. The concentration of hydrogen chloride gas in the container immediately after the closure of the bottle should be 508275. 5. Description of the invention (5) 10 minutes after using hydrogen chloride gas and 20 minutes after this application, measured using Kitgawa indicator tube (by: Himec Co., Ltd., Chugoku District Office). The initial concentration below 0.1 in Table 1 indicates the fact that 30 ppm of hydrogen chloride gas was totally adsorbed in this example. Table 1 Sample Argon Chloride Gas Concentration (ppm) After the first 10 minutes and after 20 minutes, blank 30 30 30 coffee powder 10 4 below 0.1 activated coffee powder below 0.1 lower than 0.1 lower than 0.1 Fly ash 3 0.3 less than 0.1 Activated fly ash less than 0.1 1 less than 0.1 1 less than 0.1 1 used tea leaves less than 0.1 less than 0.1 less than 0.1 activated carbon 5 2 lower than 0.1 WWm 17 8 lower than 0.1 dolomite 12 12 lower than 0.1 synthetic zeolite 1 4 0.4 lower than 0.1 1 synthetic zeolite 1 lower than 0.1 lower than 0.1 lower than 0 1 The reason why the present invention considers that the adsorption rate of the adsorption substance is important is as follows. In detail, depending on the size of the incinerator, it takes about 5 to 10 seconds or slightly different for the gasification of the combustion gas to be emitted to the atmosphere through the smokestack. During this process, the gas reacts with organic substances to make dioxin. Therefore, in the case where it takes 1 minute to adsorb the hydrogen chloride gas, dioxin is generated at this time, and the residual hydrogen chloride gas is discharged to the atmosphere. Secondly, explain in Table 1 that the initial concentration is lower than 0.1. Because the adsorbent is fine and has excellent floatability, the activated coffee powder is provided coffee, and has about 50% water content, and is dried at 100 to 140 ° C and at 100 mesh, more preferably at 200 mesh, and more preferably at Used coffee material crushed under 300 mesh. Also, because coffee powder is more easily pulverized when it has a low water content, it is preferable that -7-508275 Five 'invention description (6) is to dry it to have a water content of 2% or less. Because drying at 100t or less takes a long time, and drying at 140 ° C causes the coffee powder to penetrate the surface and its ability to adsorb hydrogen chloride gas, the drying is preferably at 120 to 130 ° C, more preferably about 125t. The adsorption rate of the used coffee powder, which is only dried to 5 to 10% water content, is poorer than that of activated carbon. The used tea leaves are dried and ground in the same way as coffee powder, and the adsorption force is only slightly worse than that of coffee powder, so that used tea leaves need to be applied in a slightly larger amount. In addition, when coffee powder and lime are used (approximately 5 to 10% by weight) or have a water content of 5 to 10%, it can be effectively and easily advantageously honed. Fly ash is a large amount of emissions from thermal power plants, and the pH is 3 to 13, depending on the type of coal used and specific equipment of the thermal power plant, so it has or shows different adsorption rates of hydrogen chloride gas. The fly ash in Table 1 shows a fly ash adsorption force having a pH of 10 (and a CEC (cation exchange force) up to about 120) by mixing various fly ash having different pH 値. Therefore, the fly ash in Table 1 is difficult to practically use. For the present invention, it is preferred to use activated fly ash provided by activating freely selected fly ash. The activation of fly ash involves mixing fly ash and slaked lime, adding water, stirring and letting stand for 2 to 3 hours. The mixing ratio of fly ash and slaked lime can be determined by oneself, but the ratio of fly ash is preferably more than slaked lime, for example, 60 to 80% by weight fly ash and 20 to 40% by weight slaked lime. The precipitate in the mixture is then dried and pulverized under a mesh size of 100 to 200, more preferably at a mesh size of 300, to obtain an excellent adsorbent showing a pH of 12 to 13 and a CEC of 150 to 200 and a relatively high rate of hydrogen chloride gas adsorption. . The synthetic zeolite is detailed next. General synthetic boiling used for synthesizing detergents, etc. 508275 V. Description of the invention (7) Stone (synthetic zeolite 1 of Table 1) has an adsorption rate that is only a little higher than activated carbon, and is therefore not good for the present invention. Another zeolite, synthetic zeolite 2 (supplied by Tosoh Corporation under the trade name " Ze ο 1 um ") shows an adsorption rate equal to the activated coffee powder and activated fly ash. " Zeolum " is excellent in adsorbing hydrogen sulfide, sulfur dioxide, or other gases such as hydrogen chloride gas, but it is problematic due to high cost. Other materials such as coconut husks, pressed soybeans, and dolomite show hydrogen chloride gas concentrations below 0.1 after gas application for 20 minutes, but cannot be used in the present invention that requires rapid adsorption. Any other adsorbent material other than those shown in Table 1 or having the same or equivalent adsorption rate as activated coffee powder and activated fly ash can be completely applied to the present invention, provided that it can be preferably obtained at low cost. Rice husks show a rather high adsorption rate when carbonized, but carbonization is cumbersome and time-consuming. Where effective carbonization methods are available, rice husks can be used in the present invention. In addition, wastes from agricultural products produced in large quantities, such as wheat husks or pressed sugar cane, can be tried as specific treatments to obtain materials showing high adsorption rates and convenience in terms of waste disposal. The dioxin generation inhibitor according to the present invention immediately or quickly adsorbs and maintains the hydrogen chloride gas generated when the waste is incinerated, and then causes the hydrogen chloride gas to react with slaked lime and / or quicklime to be eliminated. In this regard, it is preferable to use any material having an excellent reaction efficiency with respect to hydrogen chloride gas as the calcium compound. The dioxin production inhibitor according to the present invention is provided by mixing 50 to 85% by weight of a calcium compound (hydrated lime, quicklime, etc.) in an amount of 50 to 15% by weight of an adsorbing substance ', and then adding an appropriate amount of water to the mixture and granulating and drying. A better mixing ratio is 65 to 75% by weight of the calcium compound and about 35 508275 5. Description of the invention (8)

至25重量%之吸附物質,此混合比例可提供其中吸收物質 A與顆粒直徑較小之鈣化合物B比吸收物質A涵蓋大部份外 表面之戴奧辛產生抑制劑C,如第4圖之略圖所見到。真 正或實際之戴奧辛產生抑制劑包括相當大量之略示戴奧 辛產生抑制劑C組合在一起。在抑制劑C混合及接觸燃燒 氣體或廢氣時,吸附物質A立即或快速地吸附含於氣體中 之氯化氫氣體。吸附之氯化氫氣體然後反應鈣化合物B及 自燃燒氣體與廢氣之系統去除氯化鈣,而大爲抑制以氯 化氫氣體作爲材料之戴奧辛產生。Up to 25% by weight of adsorbed substance, this mixing ratio can provide the absorption of substance A and calcium compound B with a smaller particle diameter than the absorption of substance A, which covers most of the outer surface of dioxin production inhibitor C, as shown in the sketch of Figure 4. Here. The actual or actual dioxin production inhibitors include a significant amount of the dioxin production inhibitors C in combination. When the inhibitor C is mixed and contacted with the combustion gas or exhaust gas, the adsorbent A immediately or rapidly adsorbs the hydrogen chloride gas contained in the gas. The adsorbed hydrogen chloride gas then reacts with calcium compound B and removes calcium chloride from the system of combustion gas and exhaust gas, which greatly suppresses the production of dioxin using hydrogen chloride gas as a material.

依照本發明之焚燒廢棄物方法涉及將以上之戴奧辛產 生抑制劑散佈在焚燒之廢棄物上,其中本發明之粉末材 料去除燃燒氣體與飛灰中之氯化氫氣體,及粒狀材料去 除在焚燒廢棄物時產生之氯化氫氣體及含於殘餘灰中之 氯化氫氣體。粉末材料越細,其流動力越高,使得粉末 材料可具有較高之接觸燃燒氣體與廢氣效率,並且得到 優良之吸附氯化氫氣體效率。因此,依照本發明之抑制 劑採用粉末材料與粒狀材料之混合物,其混合比例可爲 約50 - 50。粉末材料可藉由使粒狀材料(粒化產物)接受粒 化器而部份地變爲粉狀,或藉由造成粒狀材料在焚化爐 中進行機械或熱(即,約450°C之燃燒熱)刺激而部份地變 爲粉狀’而簡單地或容易地提供。因此,爲了優良之降解 速率’可加入降解劑。在藉由造成粒狀材料在焚化爐中部 份地降解成粉末而提供粉末材料之情形,需要應用僅包括 粒狀材料之抑制劑,此應用易於進行。對於粒狀材料接受 -10 - 508275 五、發明説明(9 ) 粒化器之情形,或混合廢棄物之粒狀材料有效地吸附氯化 氫氣體之情形,降解速率亦爲必需的。 其次解釋降解劑。粒化及乾燥產物通常趨於較緊密。 因此,本發明提供易於降解之顆粒形狀。在加入一些降解 劑時利於降解效率。降解劑可使用有機物質,特別是植物 之硏磨產物,如榨大豆、使用過之茶葉、咖啡粉、或貝殼 之硏磨產物。可加入相對鈣化合物與吸附物質之總重量爲 約3至1 0重量%,較佳爲約5重量%之降解劑。由於太小之 顆粒直徑提供不良之降解效率,較佳爲使用直徑小於約40 至60篩目之降解劑。 本發明所指之燃燒氣體爲廢棄物在燃燒槽或區焚燒時產 生之高溫氣體。燃燒廢氣(在此或以下稱爲"廢氣")爲自燃 燒槽或區取出及排放之燃燒氣體。飛灰爲與燃燒氣體及/ 或廢氣一起飛揚之固體內容物或物質。另外,殘餘灰指來 自燃燒之殘渣。 使用火處置廢棄物涉及焚燒廢棄物以處置或利用燃燒作 爲燃料。本發明可應用於任一情形。本發明亦可應用於超 過數十至數百噸每日處置量之極大規模焚化爐或燃燒爐, 至約數十至數噸每日處置量之大或中型焚化爐或燃燒爐, 或小規模工廠或加用之小或極小型焚化爐或燃燒爐。 本發明可僅藉由將散佈器安裝在習知焚化爐或燃燒爐, 無需修改設備或新提供昂貴之設備,而應用於中型或更大 之焚化爐或燃燒爐,造成大量之成本降低。在此使用散佈 器之原因爲廢棄物由可移動地板等連續地供應,使得依照 -11- 508275 五、發明説明(1G) 本發明之抑制劑以對應每單位時間供應之廢棄物之量連續 地應用。因此,散佈器之容量必須對應指定量之廢棄物。 藉散佈器散佈抑制劑精確地對準焚燒之廢棄物。僅包括粉 末材料之本發明抑制劑需要強力進料至燃燒點。 小型焚化爐或燃燒爐可製成將散佈器安裝在外部及將散 射裝置安裝在爐內部之上部,使得實質上完全去除氯化氫 氣體。此外,小或極小型焚化爐可燃燒先與依照本發明之 抑制劑混合之廢棄物。在野外或野火燃燒時,可將依照本 發明之抑制劑散佈在廢棄物上以大爲減少或降低戴奧辛產 生。 其次解釋n RDFπ (源自垃圾之燃料,其藉由粉碎廢棄物或 垃圾,使其變硬,即,乾燥,將其壓縮及形成棒狀形狀) 。詳細言之,RDF爲藉由將含熱塑性樹脂(如塑膠膜)之廢 棄物或垃圾之材料粉碎且乾燥,及壓縮且形成指頭大小 之固態物質。由於RDF具有較少之水含量及調整良好之形 狀,其適合作爲固態燃料。由於RDF經常在材料中含氯乙 烯膜,在焚燒時RDF確實產生戴奧辛。 在此情況下,發明人嚐試在製造RDF時加入依照本發 明之戴奧辛產生抑制劑,而且成功地製造涉及較少戴奧 辛產生之RDF。習如上,在製造RDF時,加入一些生石灰 以乾燥(去除水含量)。發明人以相對乾燥廢棄物爲0 . 2至 5重量%之量加入粉狀狀態之本發明戴奧辛產生抑制劑取 代生石灰。在約〇 . 5至1 . 5重量%之負載時,特別是約0 . 7 至1重量%,提供去除戴奧辛之充分效果。 •12- 508275 五、發明説明(n) 發明之較佳Μ體實施置 (實例1 ) 將作爲鈣化合物之66重量%之高反應性生石灰(As hi da chi Lime有限公司製造,含73%之CaO)混合作爲吸附物質之 1 9重量%之活化咖啡粉(小於200篩目)與9重量%之活化飛 灰,如表1所示,及作爲降解劑之5重量%之小於40篩目 之使用過茶葉,繼而加入25重量%之水且捏合,擠製形成2 毫米X 5毫米之顆粒,及在1 20°C乾燥且形成顆粒而得到戴 奧辛產生抑制劑。 將生成之戴奧辛產生抑制劑散佈於在第1圖之小型焚 化爐(或燃燒爐)焚燒之RDF(5公斤)。散佈量爲RDF之0.7 重量%。第1圖所示之焚化爐1用於小規模工廠且在爐外部 包括散佈器2以將戴奧辛產生抑制劑進料至爐中,及散射 裝置3以將抑制劑散封在被焚燒之廢棄物上。焚化爐之容 量爲1立方米。粉末材料去除燃燒氣體與飛灰中之氯化氫 氣體’及粒狀材料去除殘餘灰中之氯化氫氣體,因而抑 制戴奧辛產生。第2圖爲散射裝置3之平面圖,其四個輪 葉3 1各在中間扭轉。 在焚燒安定時,經測量口取出燃燒氣體以測量燃燒氣 體中之氯化氫氣體濃度,及發現濃度爲118.2毫克/立方 米,如表2所示(由Himec有限公司,Chugoku區辦公室測 量)。 -13- 508275 五、發明説明(12) 表2 樣本 氯化氫氣體濃度(毫克/立方米) 實例1 118.2 比較例 442.0 (比較例1 )The method for incinerating waste according to the present invention involves dispersing the above-mentioned dioxin production inhibitor on the incinerated waste, wherein the powder material of the present invention removes combustion gas and hydrogen chloride gas in fly ash, and the granular material removes the incineration waste. Hydrogen chloride gas and hydrogen chloride gas contained in the residual ash. The finer the powder material, the higher its flow force, so that the powder material can have higher contact efficiency with combustion gas and exhaust gas, and get excellent hydrogen chloride gas adsorption efficiency. Therefore, the inhibitor according to the present invention is a mixture of a powder material and a granular material, and the mixing ratio thereof may be about 50 to 50. The powder material can be partially powdered by subjecting the granular material (granulated product) to a granulator, or by causing the granular material to be mechanically or thermally (i.e., approximately 450 ° C) in an incinerator. Burning heat) is irritating and partially powdery 'and is simply or easily provided. Therefore, a degradation agent may be added for an excellent degradation rate '. In the case of providing a powder material by causing the granular material to be partially degraded into a powder in an incinerator, it is necessary to apply an inhibitor including only the granular material, and this application is easy to perform. For the acceptance of granular materials -10-508275 V. Invention description (9) In the case of granulators, or in the case where granular materials of mixed waste effectively adsorb hydrogen chloride gas, the degradation rate is also necessary. The degradation agent is explained next. Granulated and dried products generally tend to be more compact. Therefore, the present invention provides particle shapes that are easily degraded. Degradation efficiency is facilitated when some degradation agents are added. The degrading agent may be an organic substance, particularly a plant honing product, such as pressed soybeans, used tea leaves, coffee powder, or shell honing products. A degradation agent may be added in an amount of about 3 to 10% by weight, preferably about 5% by weight, relative to the total weight of the calcium compound and the adsorbent. Since particle diameters that are too small provide poor degradation efficiency, it is preferred to use a degradation agent having a diameter of less than about 40 to 60 mesh. The combustion gas referred to in the present invention is a high-temperature gas generated when waste is incinerated in a combustion tank or zone. Combustion exhaust gas (hereinafter referred to as " exhaust gas ") is a combustion gas taken out and discharged from a self-combustion combustion tank or zone. Fly ash is a solid content or substance that flies with combustion gases and / or exhaust gases. In addition, residual ash refers to the residue from combustion. The use of fire for waste disposal involves the incineration of waste for disposal or use of combustion as fuel. The invention can be applied to any situation. The present invention can also be applied to extremely large-scale incinerators or combustion furnaces with a daily disposal volume of more than tens to hundreds of tons, to large or medium-sized incinerators or combustion furnaces with a daily disposal volume of about tens to several tons, or small scale Small or very small incinerators or burners used in factories. The invention can be applied to a medium-sized or larger incinerator or combustion furnace only by installing the diffuser in a conventional incinerator or combustion furnace without modifying equipment or newly providing expensive equipment, resulting in substantial cost reduction. The reason for using the diffuser here is that the waste is continuously supplied by the movable floor, etc., so that according to -11-508275 V. Invention Description (1G) The inhibitor of the present invention is continuously supplied in an amount corresponding to the waste supplied per unit time. application. Therefore, the capacity of the spreader must correspond to the specified amount of waste. The disperser is used to disperse the inhibitor precisely to the incinerated waste. Inhibitors of the invention that include only powder materials require a strong feed to the point of combustion. Small incinerators or burners can be made with the diffuser installed outside and the diffuser installed above the inside of the furnace so that the hydrogen chloride gas is substantially completely removed. In addition, small or very small incinerators can burn waste that has been mixed with the inhibitor according to the invention. In the wild or when wildfires are burned, the inhibitor according to the present invention can be spread on waste to greatly reduce or reduce dioxin production. Next, explain n RDFπ (a fuel derived from garbage, which pulverizes waste or garbage to make it hard, that is, dries, compresses it into a rod-like shape). In detail, RDF is a solid substance that pulverizes and dries materials containing thermoplastic resins (such as plastic films) or waste, and compresses them to form a finger-sized solid. RDF is suitable as a solid fuel because it has less water content and a well-adjusted shape. Since RDF often contains a vinyl chloride film in the material, RDF does produce dioxin during incineration. In this case, the inventors attempted to add a dioxin production inhibitor according to the present invention to the manufacture of RDF, and successfully manufactured an RDF involving less dioxin production. As mentioned above, when manufacturing RDF, add some quicklime to dry (remove water content). The inventors added the dioxin production inhibitor of the present invention in a powdered state in an amount of 0.2 to 5 wt% with respect to the dry waste to replace the quicklime. At a load of about 0.5 to 1.5% by weight, particularly about 0.7 to 1% by weight, a sufficient effect of dioxin removal is provided. • 12- 508275 V. Description of the invention (n) The best implementation of the invention (Example 1) 66% by weight of calcium compound as highly reactive quicklime (manufactured by As hi da chi Lime Co., Ltd., containing 73% by weight) CaO) mixed with 19% by weight of activated coffee powder (less than 200 mesh) as adsorbent and 9% by weight of activated fly ash, as shown in Table 1, and 5% by weight of less than 40 mesh as degrading agent After using tea leaves, 25% by weight of water was added and kneaded, extruded to form 2 mm × 5 mm particles, and dried at 120 ° C. to form particles to obtain dioxin production inhibitor. The generated dioxin production inhibitor was dispersed in the RDF (5 kg) incinerated in the small incinerator (or burner) shown in Fig. 1. The amount of dispersion was 0.7% by weight of RDF. The incinerator 1 shown in FIG. 1 is used in a small-scale factory and includes a spreader 2 outside the furnace to feed the dioxin-producing inhibitor into the furnace, and a scattering device 3 to disperse the inhibitor in the incinerated waste on. The capacity of the incinerator is 1 cubic meter. The powder material removes the hydrogen chloride gas' from the combustion gas and the fly ash, and the granular material removes the hydrogen chloride gas from the residual ash, thereby suppressing the generation of dioxin. Fig. 2 is a plan view of the scattering device 3, and each of its four blades 31 is twisted in the middle. At the time of incineration, the combustion gas was taken out through the measurement port to measure the hydrogen chloride gas concentration in the combustion gas, and the concentration was found to be 118.2 mg / m3, as shown in Table 2 (measured by Himec Co., Ltd., Chugoku District Office). -13- 508275 V. Description of the invention (12) Table 2 Samples Hydrogen chloride gas concentration (mg / m3) Example 1 118.2 Comparative example 442.0 (Comparative example 1)

RDF( 5公斤)不使用本發明之戴奧辛產生抑制劑在如實 例1之相同焚化爐中類似地燃燒。測量燃燒氣體中之氯化 氫氣體濃度,而且顯示爲442.0毫克/立方米,如表2所見 到。 ' 由以上可了解,在一般家用之小型焚化爐使用依照本 發明之戴奧辛產生抑制劑造成氯化氫氣體產生降低至約 1 /4 ° (實例2)RDF (5 kg) was similarly burned in the same incinerator as in Example 1 without using the dioxin production inhibitor of the present invention. The hydrogen chloride gas concentration in the combustion gas was measured and it was displayed as 442.0 mg / m3, as seen in Table 2. '' From the above, it can be understood that the use of the dioxin production inhibitor according to the present invention in a small incinerator for general households reduces the hydrogen chloride gas production to about 1/4 ° (Example 2)

大規模燃燒爐或焚化爐4可使用安裝在外部之抑制劑 散佈器6,如第3圖所示,進行戴奧辛產生抑制劑在廢棄 物焚燒/移動格網5上焚燒之廢棄物上之散佈。在此情形 ,原使用之燃燒爐4無需修改而僅安裝散佈器6爲足夠的 ,因而相當經濟。 RDF製造廠部份地燃燒RDF以將廢棄物材料乾燥。用於 此情形之燃燒爐可實質上具有第3圖所示之結構。製造 以1 . 5重量%之比例(相對乾燥廢棄物)混合及捏合本發明 之戴奧辛產生抑制劑之RDF (依照本發明),及習如上以2 重量%混合及捏合石灰之RDF,而且分別地在相同之大規 -14- 508275 五、發明説明(13 ) 模燃燒爐中燃燒以將廢棄物乾燥,以依照]I s K 0 3 1 1 -1 999方法及氣相層析術質量分析法測量產生之戴奧辛。 測量結果如表3所不(測重_ B a b - H i t a c h i I n d u s t r i a 1公 司)。 表3 樣本 戴奧辛(奈克-TEQ/立方米) 實例2 0.063 比較例2 0.11A large-scale burner or incinerator 4 may use an externally installed inhibitor disperser 6, as shown in FIG. 3, to disperse the dioxin-producing inhibitor on the waste incinerated on the waste incineration / mobile grid 5. In this case, it is sufficient to install the diffuser 6 without modification of the combustion furnace 4 originally used, so it is quite economical. RDF manufacturing plants partially burn RDF to dry waste materials. The combustion furnace used in this case may have substantially the structure shown in FIG. Manufacture RDF (according to the present invention) in which the dioxin production inhibitor of the present invention is mixed and kneaded at a ratio of 1.5% by weight (relatively dry waste), and RDF in which lime is mixed and kneaded at 2% by weight as described above, and separately In the same general rule -14-508275 V. Description of the invention (13) Combustion in a mold combustion furnace to dry the waste to measure in accordance with the method [Is K 0 3 1 1 -1 999] and gas chromatography mass spectrometry Born of Dioxin. The measurement results are not shown in Table 3 (weight measurement_B a b-H i t a c h i I n du s t r i a 1 company). Table 3 Sample Dioxin (Nike-TEQ / m3) Example 2 0.063 Comparative Example 2 0.11

戴奧辛:PCDDs + PCDFs + CoPCB 如表3所示,由依照本發明之RDF產生之戴奧辛爲0.063 奈克-TEQ/立方米(奈克)。此値解決已在Heisei 14( 2002) 條例指示之大規模燃燒爐之1奈克,及He 1 s en 1 4條例中新 提出之0 . 1奈克。關於家用之小型燃燒爐,條例中提出之 値各爲1 0奈克及5奈克,而且完全未造成任何問題。 (比較例2 ) 習知RDF未解決新提出之He 1 s e 1 1 4條例。在此比較例 中,部份地混合戴奧辛抑制產生劑,造成偏離實際狀態 之低產生戴奧辛値之可能性。其可由基於隨戴奧辛測量 同時取得之樣本之氯化氫氣體測量結果不具有明確差異 之事實推論,如表4所見到,即,其比較實例1與比較例 1所示之氯化氫氣體測量結果僅顯示相當不之差異,及由 參考者以下實例3與比較例3所述殘餘灰中戴奧辛濃度差 異之觀點,在表4之情形實例間僅具有相當之小差異。以 -15- 508275 五、發明説明(14) 上之推論可能亦可基於實例1與3使用小型燃燒爐’而實 例2使用大規模燃燒爐之事實及由其引起任何差異而解 釋。 表4 樣本 氯化氫氣體濃度(毫克/立方米/N) 實例2 3.9 比較例2 4.8 氯化氫氣體濃度: 〇2 12%轉化率 JIS K 0107硫氰酸汞法(II) 比吸光測定法 (實例3) 取自實例1之焚燒試驗之殘餘灰中戴奧辛濃度之測量 結果不於表5 (由:B a b - H i t a c h i I n d u s t r i a 1公司測量)。 表5 樣本 戴奧辛(奈克-TEQ/立方米) 實例3 0.033 比較例3 0.12Dioxin: PCDDs + PCDFs + CoPCB As shown in Table 3, the dioxin produced by the RDF according to the present invention is 0.063 nanograms-TEQ / cubic meter (nanograms). This solution addresses the 1 nanogram of the large-scale burner that has been instructed in the Heisei 14 (2002) regulation, and the 0.1 nanogram newly proposed in the He 1 s en 14 regulation. Regarding the small-scale burners for domestic use, the 提出 mentioned in the regulations are 10 ng and 5 ng each, without causing any problems at all. (Comparative Example 2) The conventional RDF did not resolve the newly proposed He 1 s e 1 1 4 regulation. In this comparative example, the dioxin inhibitor was partially mixed, which caused the possibility that dioxin was generated at a low deviation from the actual state. It can be inferred from the fact that the hydrogen chloride gas measurement results of the samples obtained simultaneously with the dioxin measurement do not have a clear difference, as can be seen in Table 4, that is, the hydrogen chloride gas measurement results shown in Comparative Example 1 and Comparative Example 1 only show a considerable difference. The difference, and the point of view of the difference between the dioxin concentration in the residual ash described by the referencer in Example 3 and Comparative Example 3 below, are only fairly small among the examples in the case of Table 4. With -15-508275, the inference on the description of the invention (14) may also be explained based on the fact that Examples 1 and 3 use a small-scale burner 'and Example 2 uses a large-scale burner and any differences caused by it. Table 4 Sample hydrogen chloride gas concentration (mg / m3 / N) Example 2 3.9 Comparative Example 2 4.8 Hydrogen chloride gas concentration: 〇2 12% conversion rate JIS K 0107 Mercury thiocyanate method (II) Specific absorption measurement method (Example 3) The measurement results of the dioxin concentration in the residual ash from the incineration test of Example 1 are not shown in Table 5 (measured by: Bab-Hitachi Industria 1). Table 5 Sample Dioxin (Nike-TEQ / m3) Example 3 0.033 Comparative Example 3 0.12

戴奧辛:PCDDs + PCDFs + CoPCB 毒性當量濃度 (比較例3 ) 取自比較例1之焚燒試驗之殘餘灰中戴奧辛濃度之測 量結果示於表5。 -16- 508275 五、發明説明(15) 如表5所見到,含於已散佈依照本發明戴奧辛產生抑 制劑之殘餘灰中之戴奥辛濃度比較未散佈抑制劑之情形 爲約1 / 4。依照特定之測量結果,由殘餘灰中之戴奧辛濃 度6 _ 6奈克之觀點’在本發明之比較例相當少。其推論爲 由於在此實例及比較例使用RDF作爲廢棄物材料所造成(在 此應注意,RDF混合生石灰)。 發明效果 如由以上所見到,依照本發明抑制戴奧辛產生之抑制 劑包括吸附氯化氫氣體速率優異之吸附物質,及與氯化氫 氣體之反應性優異之反應物質,作爲主要內容物,及在需 要時另外使用之降解劑,將這些材料之混合物粒化及乾 燥。 因此,戴奧辛抑制劑吸附氯化氫氣體之能力優異,而且 可大爲降低含於燃燒氣體與殘餘氣體中之戴奧辛產生, 因而對環境衛生大有貢獻。本發明亦利用工業廢棄物作爲 吸附物質,因而優於節省資源,同時提供以低成本及簡單 之裝置與技術製造之優點。 依照本發明之焚燒廢棄物方法涉及將包括粒狀材料、 粉末材料或其混合物之戴奧辛產生抑制劑散佈在被焚燒 之廢棄物上,使得粉末材料去除燃燒氣體與飛灰中之氯 化氫氣體,及粒狀材料去除殘餘灰中之氯化氫氣體,而 抑制戴奧辛產生。 依照本發明之戴奧辛產生抑制劑可對應焚燒廢棄物或 垃圾之焚化爐及燃燒爐之規模而選擇性地使用。戴奧辛 -17-Dioxin: PCDDs + PCDFs + CoPCB Toxic Equivalent Concentration (Comparative Example 3) The measurement results of dioxin concentration in the residual ash from the incineration test of Comparative Example 1 are shown in Table 5. -16-508275 V. Description of the invention (15) As can be seen from Table 5, the concentration of dioxin contained in the residual ash in which the dioxin-producing inhibitor according to the present invention has been dispersed is about 1/4 as compared with the case where the inhibitor is not dispersed. According to a specific measurement result, the view point 'from the dioxin concentration 6-6 in the residual ash' is relatively small in the comparative example of the present invention. The reasoning is due to the use of RDF as a waste material in this example and comparative examples (note that RDF is mixed with quicklime). Effects of the Invention As can be seen from the above, the inhibitors for inhibiting dioxin production according to the present invention include an adsorbent having an excellent rate of adsorbing hydrogen chloride gas, and a reactive substance having an excellent reactivity with hydrogen chloride gas, as the main content, and additionally used when necessary. Degrading agent, granulate and dry the mixture of these materials. Therefore, the dioxin inhibitor has excellent ability to adsorb hydrogen chloride gas, and can greatly reduce the production of dioxin contained in the combustion gas and the residual gas, thereby greatly contributing to environmental sanitation. The invention also utilizes industrial waste as an adsorbent, which is better than saving resources, while providing the advantages of low cost and simple device and technology manufacturing. The method for incinerating waste according to the present invention involves dispersing a dioxin production inhibitor including granular material, powder material, or a mixture thereof on the incinerated waste, so that the powder material removes combustion gas and hydrogen chloride gas in fly ash, and the granular The material removes hydrogen chloride gas from the residual ash, and inhibits the production of dioxin. The dioxin production inhibitor according to the present invention can be selectively used in accordance with the scale of incinerators and burners for incineration of waste or garbage. Dioxin -17-

_J 508275 五、發明説明(16) 產生抑制劑亦可用於不使用焚化爐等焚燒枯死之草地或 野外或野火。 因此,本發明提供以簡單之裝置(雖然迄今以相當高 之成本實行)大爲減少或降低含於廢氣之戴奧辛濃度,而 且亦大爲降低殘餘灰中之戴奧辛濃度(習知上幾乎不可肯g) ,對嚴重之環境問題提供好消息。 符號之說明 1 .....焚化爐 2 .....散佈器 3 .....散射裝置 4 .....大規模燃燒爐或焚化爐 5 .....廢棄物燃燒/移動格網 6 .....抑制劑散佈器 -18-_J 508275 V. Description of the invention (16) The production inhibitor can also be used to incinerate dead grassland or field or wildfire without using an incinerator. Therefore, the present invention provides a simple device (though it has been implemented at a relatively high cost) to greatly reduce or reduce the dioxin concentration contained in the exhaust gas, and also greatly reduces the dioxin concentration in the residual ash (which is almost unacceptable in practice). ) To provide good news for serious environmental issues. Explanation of symbols 1 ..... incinerator 2 ..... diffuser 3 .... scattering device 4 ..... large-scale combustion furnace or incinerator 5 ..... waste combustion / Mobile Grid 6 ..... Inhibitor Disperser-18-

Claims (1)

508275508275 第901 1 2491號「幾乎不產生戴奧辛之廢棄物焚燒方法,戴奧 辛產生之抑制劑及抑制劑之製法」專利案 (91年5月30曰修正) 六申請專利範圍: 1· 一種幾乎不產生戴奧辛之焚燒廢棄物方法,其係包 括: 將粒狀材料與粉末材料之混合物散佈在被焚燒之 廢棄物上;該混合物係包括作爲主要內容物之吸附 氯化氫氣體速率優異之吸附物質、及與氯化氫氣體 之反應性優異之反應物質或包括作爲主要內容物之 吸附物質與反應物質及部份易於藉機械或熱刺激而 降解成粉末材料之粒狀材料; 藉由以粉末材料來去除在燃燒氣體、廢氣與飛灰 中之氯化氫氣體,及以粒狀材料來去除在焚燒廢棄 物時產生之氯化氫氣體與殘餘灰中之氯化氫氣體以 抑制戴奧辛產生。 2.—種幾乎不產生戴奧辛之焚燒廢棄物方法,其係包 括將粒狀材料(包括作爲主要內容物之吸附氯化氫 氣體速率優異之吸附物質、及與氯化氫氣體之反應 性優異之反應物質壓縮進料至被焚燒廢棄物之燃燒 處,而去除在焚燒廢棄物時產生之氯化氫氣體及抑 制戴奧辛產生。 3.—種幾乎不產生戴奧辛之焚燒廢棄物方法,其係包 508275 六、申請專利範圍 括在焚燒操作前事先將廢棄物與 粒狀材料及/或粉末材料,其包括作爲主要內容 物之吸附氯化氫氣體速率優異之吸附物質、及與氯 化氫氣體之反應性優異之反應物質予以混合,而藉 以去除在燃燒氣體、廢氣與飛灰中之氯化氫氣體並 抑制戴奧辛產生。 4 .如申請專利範圍第1至3項中任一項之幾乎不產生 戴奧辛之焚燒廢棄物方法,其中吸附物質係使用合 成沸石、飛灰、咖啡粉、使用過茶葉、或其他之植 物廢棄物、或其中任何被活化者,及反應物質使用 氧化鈣中之至少一種化合物。 5 .如申請專利範圍第1至3項中任一項之幾乎不產生 戴奧辛之焚燒廢棄物方法,其中係在超過45〇它下 將抑制戴奧辛產生之抑制劑散佈在被焚燒之廢棄物 上;該抑制劑係包括氧化鈣與氫氧化鈣中之至少一 種化合物、及吸附氯化氫氣體速率優異之吸附物質 之粉末(如合成沸石、飛灰、咖啡粉、使用過茶葉 、其他之植物廢棄物、或其中任何被活化者)、以 及另外之淸潔劑;此等材料係被製成顆粒並乾燥; 因此造成抑制劑係部份地降解成粉末材料。 6 ·如申Sra專利$B圍弟1至3項中任—'項之幾乎不產生 戴奧羊之焚燒廢棄物方法,其中戴奧辛產生抑制劑 係以相封於廢棄物在乾燥狀態時重量爲〇 . 2至5重 508275 六、申請專利範圍 量%之比例而散佈在被焚燒之廢棄物上。 7 .如申請專利範圍第1至3項中任一項之幾乎不產生 戴奧辛之焚燒廢棄物方法,其中戴奧辛產生抑制劑 係以相對於廢棄物在乾燥狀態時重量爲〇 . 5至1 . 5 重量%之比例而散佈在被焚燒之廢棄物上。 8. —種抑制戴奧辛產生之抑制劑,其係包括粒狀材料 與粉末材料之混合物。該混合物之構成係包括用作 爲主要內容物之吸附氯化氫氣體速率優異之吸附物 質、及與氯化氫氣體之反應性優異之反應物質,或 包括作爲主要內容物之吸附物質與反應物質,及部 份易於藉機械或熱刺激降解成粉末材料之粒狀材料 〇 9 .如申請專利範圍第8項之抑制戴奧辛產生用之抑制 劑,其中吸附物質使用合成沸石、飛灰、咖啡粉、 使用過茶葉、或其他之植物廢棄物、或其中任何被 活化者,及使用氧化鈣與氫氧化鈣中之至少一種化 合物做爲反應物質。 1 〇 .如申請專利範圍第8或9項之抑制戴奧辛產生之 抑制劑,其中加入有機物質或貝殼粉來做爲降解劑 ,並且將混合材料粒化及乾燥。 1 1 . 一種製造戴奧辛產生抑制劑之方法,其係包括將 吸附氯化氫氣體速率優異之吸附物質(如合成沸石 、飛灰、咖啡粉、使用過茶葉、或其他之植物廢棄 508275 六、申請專利範圍 物、或其中任何被活化者),及氧化鈣與氫氧化鈣 中至少一種化合物之粉末予以混合,並且在需要時 加入一些有機物質或貝殼之粉末以作爲降解劑,然 後將這些混合材料粒化及乾燥。 1 2 .如申請專利範圍第1 1項之製造戴奧辛產生抑制劑 之方法,其中粒狀材料係在乾燥後經粒化器使之部 份地變爲粉末狀。 1 3 . —種製造具有較少戴奧辛產生之RDF之方法,其 係包括在壓碎、壓縮及製成固體時,將吸附氯化氫 氣體速率優異之吸附物質之粉末(如合成沸石、飛 灰、咖啡粉、使用過茶葉、或其他之植物廢棄物、 或其任何被活化者)、及氧化鈣與氫氧化鈣中至少 一種化合物之粉末之混合物,加到壓碎廢棄物之程 序。 1 4 ·如申請專利範圍第1 3項之製造具有較少戴奧辛產 生之RDF之方法,其中粉末混合物加入量之比例, 以相對乾燥廢棄物重量計係爲0 . 2至5重量%。 1 5 ·如申請專利範圍第1 3項之製造具有較少戴奧辛產 生之RDF之方法,其中粉末混合物加入量之比例, 以相對乾燥廢棄物重量計係爲0 . 5至1 . 5重量%。No. 901 1 2491 "Method of incineration of wastes that hardly produces dioxin, manufacturing method of inhibitors and inhibitors produced by dioxin" (Amended on May 30, 91) Six patent application scope: 1. A kind of dioxin that hardly produces A method for incinerating waste, which comprises: dispersing a mixture of granular material and powder material on the incinerated waste; the mixture includes an adsorbent having an excellent rate of adsorbing hydrogen chloride gas as a main content, and a hydrogen chloride gas Reactive substances with excellent reactivity or including adsorbent substances and reactive substances as the main content and granular materials that are easily degraded into powder materials by mechanical or thermal stimulation; By using powder materials to remove combustion gases and exhaust gases And the hydrogen chloride gas in the fly ash, and the granular material to remove the hydrogen chloride gas generated during the waste incineration and the hydrogen chloride gas in the residual ash to inhibit the production of dioxin. 2. A method of incineration of waste that hardly produces dioxin, which comprises compressing granular materials (including an adsorbent having an excellent rate of adsorbing hydrogen chloride gas as a main content and a reactive substance having an excellent reactivity with hydrogen chloride gas) To the burning place of the incinerated waste, to remove the hydrogen chloride gas generated during the incineration of the waste and to suppress the production of dioxin. 3. A method of incineration of waste that hardly produces dioxin, which includes 508275 6. The scope of patent application includes Prior to the incineration operation, the waste is mixed with granular material and / or powder material in advance, which includes an adsorbent having an excellent rate of adsorbing hydrogen chloride gas as a main content, and a reactive substance having an excellent reactivity with hydrogen chloride gas, thereby mixing, and thereby Removal of hydrogen chloride gas in combustion gas, exhaust gas and fly ash and inhibit the production of dioxin. 4. The method of incineration waste that generates little dioxin, such as in any one of the scope of patent applications 1 to 3, in which the adsorbent substance is synthesized Zeolite, fly ash, coffee powder, used tea leaves, or other plant waste The waste, or any of them being activated, and the reactive substance use at least one of the compounds of calcium oxide. 5. The method of incineration of waste that generates little dioxin, such as in any of claims 1 to 3 of the scope of patent application, wherein At more than 45 °, the inhibitor that inhibits dioxin production is spread on the incinerated waste; the inhibitor is a powder including at least one compound of calcium oxide and calcium hydroxide, and an adsorbent having an excellent rate of adsorbing hydrogen chloride gas. (Such as synthetic zeolite, fly ash, coffee powder, used tea leaves, other plant waste, or any of them activated), and other detergents; these materials are granulated and dried; thus causing inhibition The agent is partially degraded into a powder material. 6 · If you apply for Sra patent $ B Siege 1 to 3-the method of incineration of waste that does not produce Dior sheep, in which dioxin production inhibitor is based on phase The weight of the sealed waste in the dry state is 0.2 to 5 weights 508275 6. The proportion of the amount of patent application scope is distributed on the incinerated waste. 7. If the patent is applied for A method for incineration of waste that generates little dioxin, according to any one of items 1 to 3, wherein the dioxin production inhibitor is a ratio of 0.5 to 1.5% by weight relative to the weight of the waste in a dry state. Scattered on the incinerated waste. 8. An inhibitor that inhibits the production of dioxin, which includes a mixture of granular materials and powder materials. The composition of the mixture includes an excellent rate of hydrogen chloride gas adsorption as the main content. Adsorbent substances and reactive substances with excellent reactivity with hydrogen chloride gas, or include the adsorbent substances and reactive substances as the main content, and some granular materials that are easily degraded into powder materials by mechanical or thermal stimulation. 9 The inhibitor of dioxin production in item 8 of the patent scope, wherein the adsorption substance is synthetic zeolite, fly ash, coffee powder, used tea, or other plant waste, or any of them activated, and calcium oxide and At least one compound in calcium hydroxide is used as a reaction substance. 10. If the inhibitor of dioxin production is limited to the item 8 or 9 of the patent application scope, an organic substance or shell powder is added as a degradation agent, and the mixed material is granulated and dried. 1 1. A method for manufacturing dioxin production inhibitors, which comprises disposing of an adsorption substance (such as synthetic zeolite, fly ash, coffee powder, used tea leaves, or other plant wastes) having an excellent rate of adsorption of hydrogen chloride gas 508275 6. Scope of patent application (Or any of them activated), and powders of at least one compound of calcium oxide and calcium hydroxide, and if necessary, add some organic matter or shell powder as a degrading agent, and then granulate these mixed materials And dry. 12. The method for manufacturing dioxin production inhibitors according to item 11 of the scope of patent application, wherein the granular material is partially powdered by a granulator after being dried. 1 3. — A method for producing RDF with less dioxin production, which includes powders (such as synthetic zeolites, fly ash, coffee, etc.) that will absorb hydrogen chloride gas at an excellent rate when crushed, compressed, and made into solids Powder, used tea leaves, or other plant wastes, or any of them activated), and a mixture of powders of at least one compound of calcium oxide and calcium hydroxide is added to the crushing waste process. 14 · The method for producing RDF with less dioxin as claimed in item 13 of the scope of patent application, wherein the proportion of the powder mixture added is 0.2 to 5% by weight based on the relative dry waste weight. 15 · A method for producing RDF with less dioxin as claimed in item 13 of the scope of patent application, wherein the proportion of the powder mixture added is 0.5 to 1.5% by weight based on the weight of the relative dry waste.
TW90112491A 1999-11-25 2001-05-24 Method for burning wastes almost without generating dioxin, inhibitor of generating dioxin, and Method of producing the inhibitor TW508275B (en)

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JP33509899 1999-11-25
JP2000359970A JP2001215007A (en) 1999-11-25 2000-11-27 Refuse incineration method hardly generating dioxins and the like, dioxins and the like generation suppressing agent and its manufacturing method

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