TW527455B - Method for treating a mixture containing organic substances and white inorganic particles, material made thereby and method using the same - Google Patents
Method for treating a mixture containing organic substances and white inorganic particles, material made thereby and method using the same Download PDFInfo
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- TW527455B TW527455B TW090117420A TW90117420A TW527455B TW 527455 B TW527455 B TW 527455B TW 090117420 A TW090117420 A TW 090117420A TW 90117420 A TW90117420 A TW 90117420A TW 527455 B TW527455 B TW 527455B
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/64—Paper recycling
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527455 五、發明說明(1) [發明所屬之技術領域] 於二充作原料之廢棄物等之廢物回 戶H 應用於下述者:從含有造紙過程中.、527455 V. Description of the invention (1) [Technical field to which the invention belongs] The waste H, which is used as the raw material for waste, is returned to the household H. It should be used in the following processes:
所排出之所钢之造紙於泥等之右# T 回收高白色度之適於用於造紙等之白之混合物 由該回收(處理)方法所得 ’、、、機拉子之方法, [先前技術] '之白色無機粒子及其使用方法。 白色無機粒子係被利用以作為 劑,塗料,印品丨、、山s 市之展開附者劑,増量 以(成形品、薄膜= 產業上之内填用之填料:匕充二=等 ΐ:二i t無機粒子使用高嶺土類或碳酸鈣等之量最-“氏產口之利用形態作為代表例,加以說明。取夕之 一身又而吕,為了改盖紙 性,平滑性等,對紙漿為:;η:之光學特 料之白色無機粒子,以施行造紙。再氏;添力;=填用填 是’在改善印刷適性為主要目的者亦廣泛轭仃的 及黏合劑為主成分之翔枓泠馬:以白色無機粒子 么你田认L顏枓塗層設在紙(原紙)上。 也:甬=種内填用途或塗覆用途上之造紙用白色益機 氫氧化紹、硫化鋅、二氧化i n、 鋇、緞光白(satinwhite)、夂鈣、硫酸 以充作主體,而依照需要使:與一^化料 料(被稱為塑膠顏料)適當混合後予=種以上之有機顏The papermaking of the discharged steel is in the right of mud, etc. # T Recovers a white mixture of high whiteness suitable for use in papermaking, etc., which is obtained by the recovery (treatment) method. ] 'White inorganic particles and methods of using them. The white inorganic particles are used as agents, coatings, printed products, and printing agents in the city. The amount is (molded product, film = filler for industrial filling: dagger filling = etc.): The two inorganic particles use the most amount of kaolin clay or calcium carbonate, etc., as a representative example of the use form of "Korean production mouth." Take the example of the body and again, in order to change the paper cover, smoothness, etc., the pulp is : Η: The white inorganic particles of optical special materials, for the purpose of papermaking. Zai; Tianli; = Filling is the main purpose of improving the printability is also widely conjugated and adhesives as the main component of Xiang枓 LING MA: White inorganic particles, 你 Yan Tian L, Yan 枓 coating on paper (raw paper). Also: 甬 = white filling machine for coating or coating purposes , Indium, barium, satinwhite, satin white, calcium, and sulfuric acid as the main body, and according to need, it should be properly mixed with a chemical (known as a plastic pigment) to give more than one kind of organic Yan
C:\2D-CODE\90-ll\90ll7420.ptd 第6頁 527455 五、發明說明(2) 在另一方面,造紙產業產生所謂之造紙淤泥,此淤泥包 括:以造紙材料之紙漿等之纖維,黏合劑(如澱粉、合成黏 合劑等)為主之有機物或以上述之白色無機粒子為主之無 機物在未被利用之下被含在廢水中經過處理之固形原料; 在紙E化步驟中洗出之木質素,細微纖維,或舊紙由來造 紙用填料;附著於其上之印刷油墨;以及在生物廢水處理 步驟中所產生之剩餘淤泥等。 Λ 、該剩餘淤泥(生物廢水處理步驟中所產生者)以 要 氏淤泥之產生源為:①在造紙時通過金屬網流 在售紙處理步驟之所含異物之去除處理,脫黑’ 過程中所產生者;以及③在紙漿化 ς处理或洗加 生者,將含有此等固形物之廢水利/ /lt、過程中所產 段之固形物分離裝置予以分離及 照需要施加生物處理如活性淤泥處理二物,然後, k。經過上述處理所分離回收之後,予以放 ::ΐΓ。所產生之剩餘於泥乃成為造紙 近年來,隨著舊紙利用率之 之淤泥量變多。在其中,新:’ “二脫墨步驟由來 ’利用率高,*此相對地 ::二乂少’此類舊紙 /、淤泥產s變多。此為 3之無 於所含之無機物(無機顏沪、、、或上質舊紙 之利用峯;I;,也^ Μ ., 於泥產$較少, 機物 紙或上質舊紙之利用率為 步 紙或上質篸蟮夕』丨古上 沛隹5心售紙之利用率A ώ 八丄貝售、、、氏之利用座盔你Α 千比新聞舊 但在另一C: \ 2D-CODE \ 90-ll \ 90ll7420.ptd Page 6 527455 V. Description of the invention (2) On the other hand, the paper industry produces so-called papermaking sludge. The sludge includes fibers such as pulp made from papermaking materials. Organic substances based on binders (such as starch, synthetic binders, etc.) or inorganic substances based on the above-mentioned white inorganic particles are contained in wastewater and treated as solid raw materials without being used; in the paper E-forming step Washed out lignin, microfibers, or used paper-making fillers; printing inks attached to it; and residual sludge produced in biological wastewater treatment steps. Λ, the remaining sludge (produced in the biological wastewater treatment step) is the source of the sludge: ① during the papermaking process through the metal mesh flow in the paper sales step to remove the foreign matter contained in the treatment process, de-blacking process Producers; and ③ those who are pulping and treating or washing and regenerating, separate the waste water containing these solids / / lt, the solids separation device of the section produced in the process, and apply biological treatment such as activity if necessary The sludge treats two things, then, k. After separation and recovery from the above treatment, :: ΐΓ is placed. The remaining sludge produced becomes papermaking. In recent years, the amount of sludge has increased with the utilization of used paper. Among them, the new: "" Origin of the second deinking step "has a high utilization rate. * This is relatively:" two less. "This type of old paper / sludge produces more s. This is 3 of the inorganic substances ( Utilization peak of inorganic Yanhu ,, or high-quality old paper; I ;, also ^ Μ., The production of organic paper or high-quality old paper is less than that of high-quality old paper. Utilization of paper for sale in Shangpei 5-heart A A trophy use of helmets for sale, sale, sale, sale, sale etc
9〇117420. ptd 促m雈細+ u m之一個原因。今德泛 從進售紙之利用,必須提 7傻為了進 〇雊4售紙之利用率 527455 五、發明說明(3) $面,其利用率升高時,則會造成淤泥產量增加之新問 〇 ^於疋’為了克服淤泥之大量產生,在以往將從廢水分離 ^ t之於泥予以脫水後直接施加埋地處分之情事較多,而 機ΐίί利用流動床爐或以01"61' fUrnaCe等之焚燒爐使有 钱物燃燒以回收能量之同時’企求淤泥之減容化。 _ ΐ ϋ泥在焚燒爐燃燒時’虽隹然可將迄今未利用而廢棄之 旦、,’寻之有機物以能源有效取出回收,但由於淤泥含有大 二無機物,造成其焚燒後留存大量之殘渣(灰)之問題。 ,等,Γίί有—部分被用以混合於水泥或用於土壞改良 剐寺,而大部分以產業廢棄物經過埋地處分。 因不僅關於由焚燒回收以作為能源之有機物,亦關 用::二灰留存之無機物若能設法予以再利用以作為造紙 施ϋ甘色無機粒子(内填用之填料,塗覆用之顏料),則可 I、結果為’不僅可減低埋地處分所需要之 亦可造成目前利用率低之㈣舊紙之利用率之提高“ 但焚燒灰有下述困難:依燃燒之狀態有時減低白色卢, 或無機物(焚燒灰)之燒結進展之結&,變得粒徑不整-齊, 且大粒子化’無法直接用作造紙用之白色無機粒子。 在此種狀況之下,日本專利特開平10_0 298 1 8號 = 0-^5055號有下述倡議:㈣泥在氧氣存在之下一特日^ =有機物燃燒,而將殘存之灰再供給於焚燒爐以提Ϊ 白色度。 A捉阿 然而’上述兩公報所载之技術係回收其經過第—段之熱9〇117420. Ptd is one of the reasons to promote m + fine + u m. In order to use paper for sale, we must mention 7 in order to enter the sales rate of paper 527455. 5. Description of the invention (3) $ noodles. When the utilization rate rises, it will cause a new increase in sludge production. Question 〇 ^ Yu'In order to overcome the large amount of sludge, in the past, it is often separated from wastewater ^ t and the mud is directly dewatered after being dewatered, and the machine uses a fluidized bed furnace or 01 " 61 ' The incinerators such as fUrnaCe burn rich materials to recover energy and 'require volume reduction of sludge. _ ΐ When the mud is burned in the incinerator, 'Although it is possible to take away the unused and discarded,' 'Organic matter can be efficiently retrieved and recovered with energy, but because the sludge contains sophomore inorganic matter, a large amount of residue remains after it is incinerated. (Gray) problem. , Etc. Γίί have-some are used to mix in cement or used to improve the bad temples, and most of them are disposed of as industrial waste by buried. Because it is not only about organic matter recovered from incineration as an energy source, but also related to: If the inorganic matter remaining in the two ash can be reused as a paper-making sweet-colored inorganic particle (filler for filling, pigment for coating) , The result can be I, not only can reduce the need for buried disposal, but also can lead to an increase in the utilization rate of the old paper which has low utilization rate. However, incineration ash has the following difficulties: depending on the state of combustion, sometimes the whiteness is reduced. Lu, or the conclusion of the sintering progress of inorganic substances (incineration ash), becomes irregular and uniform in particle size, and the large particles cannot be directly used as white inorganic particles for papermaking. Under this situation, Japanese patent special Kaiping 10_0 298 1 No. 8 = 0- ^ 5055 has the following proposal: Mud mud is burned in the presence of oxygen for a special day ^ = organic matter is burned, and the remaining ash is supplied to the incinerator to improve the whiteness. A However, the technology contained in the above two communiques is to recover the heat that has passed through paragraph-
^27455 五、發明說明(4) 白色;5後::Π (.灰):利用第二段之煅燒爐來提高 之白ί产不均勺弟一段屬於藉燃燒處理之方法,所得之灰 達成而由此證實’其難於藉第二段之锻燒來 [本發明所欲解決之問題] 廢Π:全:Π性,目前急迫需要的是,減少產業 ":棄π重::::用=之=,,被要求的是, 造紙淤泥(屬於此項產業廢棄物)之利;f:目:在於提高 本發明之目的尤其在於提:ϋ =所得到之 =完全燃燒之殘留有機物以碳被白色度之改 =如之下,回收具有優異磨耗 -)之事實之 子之方法。 疋0口貝之白色無機粒 [解決問題之手段] 為解決上述問題,本發明倡I 同…泥回收白色無機方;與:常,焚捷方法不 合’使焚燒對象物所含之有機物:焚埯之場 ,燃燒廢氣而予以排出[藉以二开=邀水蒸氣等 地,本發明之目的在於由利用有=刀~此相對 化:^用煅燒處理所行之脫碳化所構:::理所行之碳 ::!機,白色無機粒子之混合物在;;/:以特徵:對 在…狀況下,下之溫 H體j存 乂化處理^ 27455 V. Description of the invention (4) White; After 5 :: Π (.ash): The second stage of the calcining furnace is used to improve the whiteness. The first stage belongs to the method of combustion treatment, and the resulting ash is reached. And it proves that 'it is difficult to use the burning of the second paragraph [problems to be solved by the present invention] waste Π: all: Π nature, what is urgently needed now is to reduce the industry ": abandon π heavy :::: With = of =, what is required is the benefit of papermaking sludge (which belongs to this industrial waste); f: purpose: to improve the purpose of the present invention, in particular to improve: ϋ = obtained = completely burned residual organic matter to Carbon is modified by whiteness = as below, the method of recycling the son of the fact that has excellent wear-).疋 0 Mussels white inorganic particles [Solutions to solve the problem] In order to solve the above problems, the present invention advocates the same as ... mud recovery of white inorganic side; and: often, the incineration method is incompatible with the organic matter contained in the incineration object: incineration In the field, the exhaust gas is burned and discharged [by two openings = invite water vapor, etc., the purpose of the present invention is to use the = knife ~ this relativeization: ^ decalcification by calcination treatment structure ::: management Carbon ::! Machine, a mixture of white inorganic particles; /: Features: Under the condition, the temperature H body j storage treatment
90117420.ptd 第9頁 527455 五、發明說明(5) "~一^---- 之步驟;對該碳化處理所得到之碳化物在一以可令該碳化 $在450 C〜1000 °C溫度範圍内氧化之方式控制之含氧氣 體之存在下施加熱處理以使脫碳化而達成白色無機粒子之 白色度為7 0 %以上之白化處理步驟。 峡化處理溫度最好能被設在至少4 5 〇 〜7 〇 〇它溫度之 圍内。 /里又 ^造紙淤泥含有紙漿殘渣成分、黏性成分等,使之乾燥 後,對含有有機物及白色無機粒子之混合物在限制含氧氣 體之。存在之貧氧狀態下,且在45〇 t〜65〇 以5〇〇〜” 6 0 0 C較佳)溫度下施加碳化處理3 〇〜6 〇分鐘。然後,利用 連續式或分批式等形式之煅燒爐,在45〇〜65〇。〇(以5〇〇 °C〜6 0 0 °C較佳)溫度下予以煅燒6〇〜18〇分鐘。 最好能按至少二階段之溫度施行碳化處理。更佳的是, 碳化處理係屬於間接加熱者。 亦較佳的是,按至少二階段之溫度施行藉脫碳之白化 (暫時以’’脫碳-白化’,表示之,以下皆同)處理。更佳的 是,白化處理係屬於間接加熱者。 在上述混合物含有高嶺石之場合,較佳的是,以可令高 嶺石非晶質化之方式控制脫碳—白化處理。 依照含氧氣體之供給量將脫碳-白化處理溫度調節為8〇〇 °C以下。 ” 最好能在碳化處理及脫碳-白化處理之期間,使處理對 象物一旦冷卻至40 0 °C以下之溫度後,施行其後之處理。 較佳的是,使處理對象物在與水及/或水蒸氣接觸之下90117420.ptd Page 9 527455 V. Description of the invention (5) " ~ 一 ^ ---- steps; the carbides obtained by the carbonization treatment can make the carbonization at 450 C ~ 1000 ° C In the presence of an oxygen-containing gas controlled in an oxidation manner in a temperature range, heat treatment is applied to decarburize to achieve a whitening step in which the whiteness of the white inorganic particles is 70% or more. The temperature of the fracturing treatment can preferably be set within a range of at least 450 to 700 ° C. The papermaking sludge contains pulp residue components, viscous components, etc. After drying, the mixture containing organic matter and white inorganic particles is restricted to oxygen-containing gas. Under the existing oxygen-depleted state, the carbonization treatment is applied at a temperature of 45 ° to 65 ° and 50 ° to 60 ° C (preferably) for 3 to 60 minutes. Then, a continuous method or a batch method is used. The calcining furnace in the form is calcined at a temperature of 4500 to 65.0 (preferably at 500 ° C to 600 ° C) for 60 to 180 minutes. It can be performed at a temperature of at least two stages. Carbonization treatment. More preferably, the carbonization treatment belongs to indirect heating. It is also preferable that the whitening by decarbonization is performed at a temperature of at least two stages (temporarily decarburization-whitening), which is indicated below. Same) treatment. More preferably, the whitening treatment belongs to indirect heating. In the case where the mixture contains kaolinite, it is preferable to control the decarburization-whitening treatment in such a way that the kaolinite can be made amorphous. The supply amount of the oxygen-containing gas is adjusted to a temperature of decarburization-blanching treatment below 800 ° C. "It is desirable that the object to be treated can be cooled below 40 ° C once during the carbonization treatment and decarbonization-blanching treatment. After the temperature, the subsequent treatment is performed. Preferably, the object to be treated is brought into contact with water and / or water vapor
C:\2D-C0DE\90-ll\90117420.ptd 第10頁 527455 五、發明說明(β) 冷部。 主白色無機粒子之混合物為以造紙於泥為 車六*茱物及/低級舊紙之場合亦可應用上述方法。 稀以I,將所回收之白色無機粒子使用水性媒體予以 〜^ :到水性懸洋液,繼之調整該水性懸浮液之ΡΗ為8 之後予以使用。 之ί:更佳的是,利用二氧化碳來調整上述水性懸浮液 Ρ為8〜1 3之後,予以使用。 [發明之實施形態] 圖Γ為在/f圖1之下,關於本發明之回收步驟加以說明。 在本Λ 回收白色無機粒子之方法之程序圖。51為 ΐ ^當原!!之於泥。其次,52為包括乾燥、熱分 此等:Γ反化之;。53為終白化處理步驟。將 游::脫碟!驟總稱為熱處理步驟。經過熱處理後之 步賢後口收為白機粒子,而54為粉碎步驟。經過此等 說明各步驟。 丹生為顏料、填料等。以下 (淤泥) 淤泥51為從汚水(存在於下水道、 ^ r ^ 產生之廢棄物。污水或工廠廢水由於:f二)、,n 經過澄清器或凝聚沈澱槽沈降分離::形物乂之 際,以廢棄物含在廢水内之固形物:以放:來;: M β J从/於泥#回收0通φ 水或焚燒:地廢棄。在本實施形態之情 況’使淤泥經過硤化處理及脫碳—白化處理,藉此施行顏C: \ 2D-C0DE \ 90-ll \ 90117420.ptd Page 10 527455 5. Description of the invention (β) Cold section. The above method can also be applied in the case where the mixture of the main white inorganic particles is made of paper, mud, or sapwood and / or low-grade old paper. Dilute the white inorganic particles with I using an aqueous medium ~ ^: to an aqueous suspension, and then adjust the pH of the aqueous suspension to 8 and use it. It is more preferable to use carbon dioxide to adjust the above-mentioned aqueous suspension P to 8 to 13 before use. [Embodiment Mode of the Invention] FIG. Γ illustrates the recovery steps of the present invention under / f FIG. 1. The procedure of the method of recovering white inorganic particles in this Λ. 51 for ΐ 当 Dangyuan !! of mud. Secondly, 52 includes drying, thermal separation, etc .: Γ reverses it; 53 is a final whitening process step. Will swim :: off! This step is collectively referred to as a heat treatment step. After the heat treatment, the steps are collected into white machine particles, and 54 is the crushing step. After these steps are explained. Dansheng is pigment, filler and so on. The following (sludge) Sludge 51 is the waste generated from sewage (existing in the sewer, ^ r ^. Sewage or factory wastewater due to: f 二) ,, n Settled and separated by a clarifier or a coalescence sedimentation tank :: When the material is 乂The solids contained in the waste water by waste: put: come ;: M β J recovers 0 through φ water from / in mud # or incineration: ground waste. In the case of this embodiment mode, the sludge is subjected to a desulfurization treatment and a decarburization-whitening treatment, thereby performing a color
C:\2D-CODE\90-ll\90117420.ptdC: \ 2D-CODE \ 90-ll \ 90117420.ptd
52^45552 ^ 455
五、發明説明(7) 料之再生。另外,亦可使用低級舊紙(含有大量之雜諸雀 紙等之不純物,難於再利用以作為造紙原料者)或所附^ 之塑膠為主之 R P F (R e f u s e d P a p e r & P 1 a s t i c F u e 1 )為 料。在造紙原料之使用有關之本發明中,造紙原料由“'來^ 淤泥為較佳之原料,因此,以下關於使用造紙原料由來 於泥之例子加以敘述。造紙於泥之來源為從紙漿製造+ 驟、舊紙再生步驟、以及造紙步驟流失之廢水(包括日夂 所稱之”排水”,以下皆同)中之固形物。 按固形分比率基準時,最 下較佳。大量含鐵之游泥 題。關於減低鐵量之方 造紙工場廢水處理步驟中 之凝聚劑。再者,有可行 以除去混入淤泥中之鐵片 無法混入。此外,較佳的 大燒結塊子。此等異物去 象物之形態以可有效去除 -白化處理,粉碎處理等 ’儘量在前段之步驟施行 份或%均為有效成分之份 化前,先粒化(製粒)後再 ’細微粒子則會一體化, 高碳化後之效率。再者,V. Description of the invention (7) Regeneration of materials. In addition, low-level old paper (containing a lot of impurities such as miscellaneous paper, which is difficult to reuse as a raw material for papermaking) or RPF (R efused P aper & P 1 astic F) ue 1) is expected. In the present invention relating to the use of papermaking raw materials, the papermaking raw materials are made from "'sludge'. Sludge is the preferred raw material. Therefore, the following examples of the use of papermaking raw materials are derived from sludge. The source of papermaking from sludge is made from pulp + , Waste paper recycling step, and the waste water lost in the papermaking step (including the "drainage" referred to by the sundial, the same applies hereinafter). The solid content ratio is the best. The large amount of iron-containing sludge Question. Regarding the coagulant in the waste water treatment step of the square paper mill to reduce the amount of iron. Furthermore, it is feasible to remove the iron flakes mixed in the sludge and cannot be mixed. In addition, the preferred large sintered blocks. These foreign matter removal objects The form can be effectively removed-whitening treatment, pulverization treatment, etc. 'As far as possible in the previous step, the ingredients or% are effective ingredients. Before granulation, granulation (granulation) and then' fine particles will be integrated, high Efficiency after carbonization. Furthermore,
又按,淤泥中之鐵分(Fe含量) 好能為5.0wt%以下,以3.〇wt%以 會造成無法充分提高白色度之問 法,較佳的是,例如為凝聚劑在 被用以分離固形物者使用未含鐵 性的是,在分級機設置磁鐵等, 包括鐵絲、鐵釘等,或設法使之 疋’依照需要施行去除異物或粗 除處理最好能配合淤泥及去除對 之方式予以設在碳化處理、脫碳 之各處理步驟之間,而更佳的是 去除。又按,本說明書中所示之 (重量)或w ΐ %,除非另有註明。 亦有可行性的是,將淤泥在石炭 予以碳化。經過此項粒化處理後 可防止細微粒子之飛散,而可提According to another, the iron content (Fe content) in the sludge can be 5.0% by weight or less, and 3.0% by weight may cause a problem that the whiteness cannot be sufficiently improved. Preferably, for example, a coagulant is used. To separate solids, use non-ferrous materials, install magnets, including iron wires, nails, etc. in the classifier, or try to make them 'remove foreign matter or rough removal according to needs. It is best to cooperate with sludge and remove The method is provided between the carbonization treatment and decarburization treatment steps, and more preferably, it is removed. Again, (weight) or w ΐ% shown in this specification, unless otherwise noted. It is also feasible to carbonize the sludge on charcoal. After this granulation treatment, fine particles can be prevented from scattering, and
i、發明說明(8) (由於粒化),极; 、, 好之效率實現古^大小之變動變小,碳化效率升高,以良 對含水狀態之之熱分解,而可達成設備之小型化° 等之方、去來#:化然亦可利用滚動粒化法、攪拌粒化法 *,則在=口:::但若採用乾燥於泥之壓縮成形之方 關於乾式之粒化;:、、’勺熱能,因此較佳。 等之壓縮成形機。’最好能使用壓團機、滾式壓實機 桿強制擠入被加题用此等壓縮成形機時,將游泥藉螺 縮成形。土之兩輕之間,而使輥子旋轉即可進行壓 (碳化步驟) 在碳化步驟5 2施行淤、、尸—^ 之固形分(固形物含量=乾燥及藉熱分解之碳化。游泥 水機之能力而不同。=在5%〜60%之範圍内’因為依脫 使含水於泥乾燥。使i =最好能在碳化步驟之前半期間 姐女士 使,於,尼乾燥時,可藉此有效達成熱分 ’、有可能在未區別淤泥之乾燥與熱分解之下施行碳化 =理i不過更佳的是,各別設置乾燥之溫度帶及熱分解之 恤度帶。即在淤泥之碳化處理中,由於有機物之乾燥溫度 與其熱分解溫度不同而設置二階段以上之加熱帶時,可藉 此有效達成淤泥之碳化。 若依照習知技術之焚燒處理方法按80 0 °C以上之高溫充 分供給氧氣之焚燒(燃燒)條件,則可推斷(碳化處理之結 果)如下:紙漿成分等之物質被燃燒’二氧化矽等之類熔融 生長於所殘留之碳之周圍而形成殘渣,變為帶黑色之固形 物,於是黏土成分原有之構造被破壞。i. Description of the invention (8) (due to granulation), extremely good efficiency, small change in the size of the ancient ^ size, increased carbonization efficiency, good thermal decomposition of the water-containing state, and can achieve small equipment化 ° 等 方 、 去 来 #: Huaran can also use rolling granulation method, stirring granulation method *, then == :: But if using the compression molding method dried on mud, about dry granulation ;: ,, 'spoon heat energy, so better. And other compression molding machines. It is desirable to use a compactor or a roller compactor to force the rod into a compression molding machine to be used, and then use the screw to form the mud. The soil is light, and the roller can be pressed to rotate (carbonization step). In the carbonization step 52, the solid content of the sludge, corpse, and ^ (solid content = drying and carbonization by thermal decomposition. Sludge water machine) The ability is different. = Within the range of 5% to 60% 'because the hydrated mud is dried by ITO. It is best to use it during the first half of the carbonization step. Effectively achieving thermal points', it is possible to perform carbonization without distinguishing between the drying and thermal decomposition of the sludge. However, it is better to set a dry temperature zone and a thermal decomposition shirt separately. That is, the carbonization of the sludge. In the process, because the drying temperature of the organic matter is different from its thermal decomposition temperature, when the heating zone is set at two or more stages, the carbonization of the sludge can be effectively achieved. If the incineration treatment method according to the conventional technology is sufficiently high at 80 ° C or higher The incineration (combustion) conditions of oxygen supply can be inferred (results of carbonization treatment) as follows: pulp and other substances are burned and 'silicon dioxide' and the like are melted and grown around the remaining carbon to form residues. The solid black band was then clay component of the original structure is destroyed.
illill
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527455 五、發明說明(10) 雖然有機物由來 能以可達成有機 保持原狀之方式 在碳化步驟中 物之燃燒同時發 之燃燒,焚燒對 上,造成淤泥所 化步驟中限制含 之發火所引起之 儘量使淤泥在被 需要之尺寸設置 氧氣體(空氣)存 泥所產生之水蒸 以置換。更佳的 氧氣存在於爐内 為於泥之加熱 經濟觀點上最好 有可能利用燃燒 之氧氣(空氣)與 淤泥不致與熱風 之碳化設備,最 更佳的是5碳化 熱用之加熱室所 碳化時之加熱 之碳與 物由來 施行碳 若有氧 生有機 象物之 含顏料 氧氣體 爐内氣 投入時 投入口 在於爐 氣或揮 是,使 碳酸約 之碳之 化處理 氣之存 物之燃 燃燒溫 之不被 (空氣) 氛溫度 不伴隨 之大小 内之場 發性成 爐内變 由來之碳難於區別,但最好 固定碳化且碳酸鈣由來之石反 在,則 燒。其 度上升 希望之 之流入 以上之 氧氣之 。亦有 合,不 會與於 結果是 至爐内 熱變性時,可 升溫。 方式’ 可能於 過較佳 分(一氧化石反 成貧氧狀態’ 泥所含 ,由於 之氣氛 。因此 藉此防 較佳的 按最低 泥所伴 的是, •氫氣) 即實質 之揮發 有機物 溫度以 ,在碳 止淤泥 是,以 限度所 隨之含 利用於 迅速予 上並益 「 「- φ\\\ 方法,雖 能利用燈 氣體來施 淤泥接觸 直接接觸 好能使用 裝置為由 構成之雙 方法為, 然用電加熱亦有可行性,不過在 油或重油之燃燒氣體來加熱。,亦 行直接加熱,不過由於熱風所含 ’致使淤泥發火燃燒,最好能以 之方式設置隔牆。因此,為;尸 可限制空氣流入之密閉室。即了 雄閉式之淤泥碳化室與碳化h 重構造之間接加熱爐。 至加 將燃燒氣體壓送至加孰室 …'至’错此527455 V. Description of the invention (10) Although the organic matter can be burned simultaneously in the carbonization step in a way that can maintain the original state of the organic matter, the incineration is opposite, resulting in as far as possible the fire caused by the limitation of the sludge formation step. The silt is steamed to replace the water produced by setting the oxygen gas (air) in the required size. Better oxygen exists in the furnace for the heating of the mud. From the economic point of view, it is best to use the carbonization equipment that burns the oxygen (air) and the sludge to prevent hot air. The most preferable is the carbonization of the heating chamber for 5 carbonization heat. The heating of carbon and materials from the beginning of the implementation of carbon if there are aerobic organic matter, pigment-containing oxygen gas furnace gas input when the input is in the furnace gas or vapour, so that the carbonization of the carbonized carbon treatment gas storage Combustion temperature is not affected by (air) The temperature within the range that does not accompany the temperature of the atmosphere is difficult to distinguish from the carbon generated in the furnace. However, it is best to fix the carbonization and the calcium carbonate derived stone is in reverse, then burn. The degree of hope rises into the above oxygen. There is also a combination that will not increase the temperature when the result is thermal denaturation in the furnace. The method 'may be too good (the monoxide is turned into an oxygen-depleted state') because of the atmosphere contained in the mud. Therefore, it is better to prevent the lowest mud accompanied by hydrogen, which is the temperature of the volatile organic matter. Therefore, in the carbon to stop the sludge, the limit is used to quickly and benefit from the "-φ \\\ method. Although the lamp gas can be used to contact the sludge, the direct contact is good. The method is that although electric heating is also feasible, but it is heated by the combustion gas of oil or heavy oil. Direct heating is also possible, but because the mud contained in the hot air causes the silt to ignite and burn, it is better to install partition walls in this way. Therefore, the closed chamber which can restrict the inflow of air. That is, the heating furnace is connected between the sludge carbonization chamber and the carbonization h heavy structure.
90117420.ptd 527455 五、發明說明(11) 加熱淤泥以使乾燥。為燃燒氣體,90117420.ptd 527455 V. Description of the invention (11) Heating the sludge to dry it. Is the combustion gas,
備所排出之燃燒氣體。為焚燒設備之^用從現有之焚燒設 (如stoker furnace之型式)、散希、->1式可例示爐篦式 熱風燃燒式等。當然亦有可能式二材料授拌式、 器,藉此直接加熱其淤泥加熱室,^熱至内設置燃燒 爐之外部設置燃燒器,藉此產生燦掉^ $可能在間接加熱 在齡泥乾燥後’將乾燥於泥加熱,1月豆 機物分解。此際,會產生一氧化噢错此使淤泥所含之有 氣體,但由於爐内實質未含氧氣,口甲烷、乙烷等之可燃 可將可燃氣體吸入熱風產生裝置,可抑制有機物之燃燒。 化上之熱源。 以作為淤泥之乾燥及碳 (脫碳-白化處理步驟) 其次,在白化處理步驟53施行碳化 脫石炭-白化處理步驟中,使碳化物所人勿之^石反—白化。在 料。由於高熱量之可燃氣;以;然後回收白色無機彥 未存在於爐内,可抑制揎蓼刖 碳化步驟中揮發^Prepare the exhaust gas. For the use of incineration equipment, the existing incineration equipment (such as the type of stoker furnace), Sanxi, and-> type 1 can be exemplified by the grate type and the hot air combustion type. Of course, it is also possible to heat the sludge heating chamber directly by using the two-material mixing type heater, and set the burner on the outside to set the combustion furnace inside, thereby generating bright ^ $ may be indirect heating in the aging mud drying After the 'drying in mud', the beans are decomposed in January. At this time, there will be oxidization, and the gas contained in the sludge will be generated. However, because the furnace contains substantially no oxygen, methane, ethane, etc. are combustible. Combustible gas can be sucked into the hot air generating device, which can suppress the combustion of organic matter. The heat source of transformation. Drying and carbon as sludge (decarbonization-whitening treatment step) Secondly, in the whitening treatment step 53, carbonization and decarbonization-whitening treatment steps are performed to make the carbides away from stone-whitening. In the material. Due to the high heat of flammable gas; to; then recovering the white inorganic cyanide does not exist in the furnace, which can suppress the volatilization in the carbonization step ^
以上之燃,堯。因&,可之燃燒所引起之爐崎 含白色無機粒子之不被希幾物之燃燒所引起之淤泥片 脫碳-白化處理步驟中,处、、、變性。即在碳化步驟後$ 上所需要之氧氣(空氣〕。L可%充分供給在碳化物之氧化 此,由於前段之碳化步^狀恶被稱為富氧狀態。如 合,最後可在合適之條段脫碳-白化處理步驟之組 將脫碳-白化室以复m白色無機粒子白化。 皿度可達到45(rc 〜100(rc範圍内^The burning of the above, Yao. Furnazaki caused by & burnable sludge flakes caused by burning of white inorganic particles that are not burned by Greeks Decarbonization-whitening step, denaturation. That is, the oxygen (air) required after the carbonization step. L can be fully supplied to the oxidation of the carbide. Due to the carbonization step in the previous stage, the evil is called an oxygen-enriched state. The group of strip decarburization-whitening treatment steps will whiten the decarburization-whitening chamber with white inorganic particles. The degree of dishing can reach 45 (rc ~ 100 (rc range ^)
527455 五、發明說明(12) 溫度之方式予以加熱時,可藉此有效提高白色度。在脫碳 -白化室内,由於將爐内之氣氛溫度設定為5 〇 〇艺以上,碳 化物所含之有機物由來之碳被氧化,可達成白色無機粒子 之有效白化。 脫竣-白化若在低於45 0 °C之溫度下進行,其處理時間則 變長,而若在超過丨0 0 0 t之高溫下進行,白色無機粒子之 , 熔融·燒結則會進展,致使脫碳-白化後之微粉碎發生困 難’除了此種缺點之外,又加強著色傾向,因此均不合 適。關於處理時間,不僅應根據碳化物之形態、質量、水 分、以及碳含量,亦應根據經濟效果,以及環境上之觀^ 加以考慮’不過以3 〇分鐘至2小時之程度較佳。最後,使 碳化物脫碳而使白色無機粒子之白色度達到7 〇 %以上(以 8 0%以上較佳)時,可藉此製成一種適於造紙用原料之 無機粒子。 @ & 尤其可提的是,脫碳-白化處理步驟亦被稱為煅燒處 之步驟。在此一步驟藉一段處理進行之場合,在450它〜 6 50 °C (以5 0 0 °C〜6 0 0 °C較佳)溫度下且在富氧狀態下炮 60〜180分鐘時,可推斷其結果是,發生碳化物之燃^ a 而碳酸鈣、高嶺土、二氧化矽等之無機成分以再使用心, 成問題之程度殘留下來。在溫度低於4 5 〇時,有機 不 之碳化則很難進展,而在溫度超過65〇 Ό時,黏土成,= 之構造則容易被破壞,因此為了得到安定之再生材刀等 好能在配合造紙淤泥之成分之下調整處理溫度之範圍,最 在脫碳-白化處理步驟中,若急劇加熱碳化物,白。527455 V. Description of the invention (12) When heated by temperature, it can effectively improve the whiteness. In the decarburization-whitening room, since the temperature of the atmosphere in the furnace is set to 5,000 or more, the carbon derived from the organic matter contained in the carbide is oxidized, and the effective whitening of the white inorganic particles can be achieved. Decomposition-whitening is performed at a temperature lower than 45 0 ° C, and the treatment time becomes longer. If it is performed at a high temperature exceeding 丨 0 0 t, the melting and sintering of white inorganic particles will progress. Causes difficulty in fine pulverization after decarburization-whitening. In addition to this disadvantage, it also enhances the coloring tendency, so it is not suitable. Regarding the treatment time, it should be considered not only in terms of the form, quality, moisture, and carbon content of the carbide, but also in terms of economic effects and environmental aspects ^, but it is preferably about 30 minutes to 2 hours. Finally, when the carbide is decarburized and the whiteness of the white inorganic particles reaches 70% or more (preferably 80% or more), an inorganic particle suitable for a raw material for papermaking can be produced by using this. @ & In particular, the decarburization-whitening treatment step is also referred to as the calcination step. In the case where this step is carried out by a piece of processing, at a temperature of 450 to 6 50 ° C (preferably 5 0 ° C to 6 0 ° C) and 60 to 180 minutes in an oxygen-rich state, As a result, it can be inferred that the combustion of carbides occurred, and the inorganic components such as calcium carbonate, kaolin, and silicon dioxide were reused, and the extent of the problem remained. When the temperature is lower than 450, organic carbonization is difficult to progress, and when the temperature exceeds 65 ° C, clay formation is easily destroyed, so in order to obtain a stable recycled material knife The range of the processing temperature is adjusted to match the components of the papermaking sludge. In the decarburization-whitening treatment step, if the carbide is heated rapidly, it will become white.
527455 五、發明說明(13) 機粒子之炼融〜燒社 機粒子中,致使而碳分子被收容於白色無 熱,更佳的是,Γ 以:;為:防止竣化物之急劇加 理。在脫碳—白化處理γ又W之溫度帶施行脫碳-白化處 _ot:〜100〇t: pt;^M,45(rc〜60〇°c 段以上之熱處理中,—/ϋ更多階段之加熱帶。在二階 溫度不致升高至的疋,以其後段使處理對象物之 際,更佳的是,;上之方式在前段施行脫碳。此 性溫度變化係難於測f 土物本身之溫度。但碳化物之局部 置溫度感測器,以白2 A。因此’較佳的I,在白化室設 方式,供給含氧氣於(/^氣氛溫度可達到80 0 °cu下之 所引起之碳化物(本;:二)2 =致發生碳化物之自燃 4身之)溫度之急劇上升之方式予以管 理0 在處理前之於泥合古1山 石之方式控制碳化—白化7員二之场Λ ’以可有效減少高嶺527455 V. Description of the invention (13) Melting and melting of organic particles ~ Burning of organic particles, so that the carbon molecules are contained in white and no heat. More preferably, Γ is: to prevent sharp processing of finished compounds. In the decarburization-whitening treatment γ and W temperature zone, decarburization-whitening is performed_ot: ~ 100〇t: pt; ^ M, 45 (rc ~ 60 ° ° c or more in the heat treatment,-/ ϋMore The heating zone of the stage. When the second-stage temperature does not increase to 疋, and the subsequent stage makes the object to be treated, it is more preferable to perform decarburization in the preceding stage. The temperature change of this property is difficult to measure f soil The temperature itself. But the localized temperature sensor of the carbide is white 2 A. Therefore, the 'better I' is set in the whitening room to supply oxygen containing (/ ^ atmosphere temperature can reach 80 0 ° cu. The resulting carbides (this;: two) 2 = caused by the temperature of the spontaneous combustion of carbides to be controlled by a rapid rise in temperature Ninomiya Λ 'to effectively reduce kaolin
、 曰色度。此係由於在450 C〜1000 °C 之脫碳-白化處理步驟中,使高嶺石非晶質化而變性至形 成高白色度之煅燒高嶺土所致。因此’將碳化_白化處理 步驟之處理溫度設定為450。(:〜1 0 0 0。(:時,可藉此達成淤 泥原來所含之白色無機粒子之白色度以上之白色度。為了 防止白色無機粒子之熔融〜燒結,更佳的是,設定為6 〇 〇 〇C 〜9 0 0 〇C。 但疋,重要的是,在處理前之淤泥含有高嶺石及碳酸鈣, Said chroma. This is due to the denaturation of kaolinite in the decarburization-whitening treatment step at 450 C ~ 1000 ° C to denatured to form a high whiteness calcined kaolin. Therefore, the processing temperature of the carbonization-whitening process step is set to 450. (: ~ 1 0 0 0. (: can be used to achieve whiteness above the whiteness of the white inorganic particles originally contained in the sludge. To prevent the white inorganic particles from melting to sintering, it is more preferable to set it to 6 〇〇〇C ~ 900 〇C. However, it is important that the sludge before treatment contains kaolinite and calcium carbonate
527455 五、發明說明(14) 之場合,考慮到下述情況之影響:即碳酸鈣與煅燒高嶺石 起反應而發生白色無機粒子之溶融〜燒結。此等白色無機 粒子除了有使脫碳-白化後之微粉碎發生困難之不便之 外,亦有增強著色傾向之缺點,因此不合適。 雖然上述情況依碳酸鈣含量而不同,但為了在防止白色 無機粒子之炫融〜燒結之下,提高高嶺石之白色度,最好 能管理碳化物本身之溫度。但碳化物之局部性溫度變化係 難於測定。因此,較佳的是,在白化室設置溫度感測器, 以白化室之氣氛溫度可達到8 0 0 °C以下之方式,供給含氧 氣體(空氣),而以不致發生碳化物之自燃所引起之碳化物 (本身之)溫度之急劇上升之方式予以管理。又按,高嶺石 為屬於2八面體型1 : 1層狀矽酸鹽,其除了包括狹義之高嶺 石外,亦包括多水型之地開石(d i c k i t e )、珍珠陶土 (nacrite)、以及敘永石(ha 1 1 oy s i te ) o 由於要防止碳酸妈之脫碳酸’在脫碳後之白色無機粒子 會混有來自於泥之碳酸釣。因此,白色無機粒子之殘碳率 有時在脫碳-白化處理後亦顯示較高之數值。雖然有機物 由來之碳與碳酸鈣由來之碳難於區別,不過較佳的是,儘 量降低有機物由來之殘碳率。最好能將有機物由來之殘碳 率設定為1 %以下,藉以回收適於造紙之白色無機粒子。 為碳化物之加熱方法,亦有可能利用燃燒氣體來施行直 接加熱,但此項直接加熱引起熱風所含之未燃碳與白化之 白色無機粒子接觸,致使白色度降低,因此,最好能以於 泥不致與熱風直接接觸之方式設置隔牆。即,在脫碳—白527455 5. In the case of the description of the invention (14), the influence of the following conditions is taken into consideration: that is, calcium carbonate reacts with the calcined kaolinite and the white inorganic particles are melted to sinter. These white inorganic particles are not suitable in addition to the inconvenience of making micro-pulverization after decarburization-whitening difficult, and also have the disadvantage of enhancing the coloring tendency. Although the above conditions vary depending on the calcium carbonate content, it is best to manage the temperature of the carbide itself in order to increase the whiteness of kaolinite while preventing the white inorganic particles from sintering to sintering. However, the local temperature change of carbides is difficult to measure. Therefore, it is preferable to provide a temperature sensor in the albino chamber so that the atmosphere temperature of the albino chamber can reach below 80 ° C to supply an oxygen-containing gas (air) so that the spontaneous combustion of carbides does not occur. The resulting sharp rise in the temperature of the carbide itself is managed. According to another, kaolinite is a octahedral type 1: 1 layered silicate, which includes not only kaolinite in a narrow sense, but also water-based dickite, pearlite, and Syria Yong Shi (ha 1 1 oy si te) o To prevent the decarbonation of carbonic acid, the white inorganic particles after decarburization will be mixed with carbonic acid from mud. Therefore, the residual carbon ratio of the white inorganic particles sometimes shows a higher value after the decarburization-whitening treatment. Although the carbon derived from organic matter is difficult to distinguish from the carbon derived from calcium carbonate, it is preferable to reduce the residual carbon rate derived from organic matter as much as possible. It is best to set the residual carbon ratio from organic matter to 1% or less, so as to recover white inorganic particles suitable for papermaking. For the heating method of carbides, it is also possible to use combustion gas to perform direct heating, but this direct heating causes the unburned carbon contained in the hot air to contact the whitened white inorganic particles, resulting in a decrease in whiteness. Therefore, it is best to use Set up partition walls in such a way that the mud does not come into direct contact with hot air. That is, in decarburization-white
527455 五、發明說明(15) 化處理步驟亦與碳化步驟一樣,更佳的是,其加熱爐為由 密閉式之碳化物脫碳-白化室與加熱室所構成之雙重構造 之間接加熱爐。 加熱室以電加熱雖然亦有可行性,不過在經濟觀點上最 好能利用燈油或重油之燃燒氣體來加熱。回收上述丨於泥由 來之揮發氣體後使之燃燒所得到之熱風亦可予以使用。此 外’也可使用其他現有之焚燒設備如焚燒爐等所排出之燃 燒氣體。焚燒設備之型式可例示爐篦式(如st〇ker furnace之型式)、散布浮游式、材料攪拌式、熱風燃燒式 等。 ’ 此外,以廢水處理裝置之一部分被設置於各造紙工場之 旋窯或現有之焚燒爐(旋風爐或流動焚燒爐)均可予以使 用’而更佳的是,使用一種有可能施行長時間之脫碳一白 化處理之旋窯。 再者,在碳化處理及脫碳-白化處理之期間,使處理對 象物一旦冷卻至400 °C以下之溫度後,再施行其後之處理 時,可藉此從碳化物完全除去因碳化處理被熱分解之有機 物由來之可燃氣體。此外,在此期間使碳化物與水及/或 水蒸氣接觸而冷卻時,可藉此增加碳化物之比表面積,提 高脫碳-白化處理步驟上之處理物與氧氣之反應效率,而 有效進行脫碳-白化處理。 在連續進行碳化及脫碳-白化之場合,在熱處理室内設 置螺桿或攪拌葉片時,可藉此強制移送淤泥或碳化物。用 螺桿強制擠入時,可藉此促進攪拌,而提高埶處理效率。527455 V. Description of the invention (15) The chemical treatment step is the same as the carbonization step. More preferably, the heating furnace is a double structure indirect heating furnace composed of a closed carbide decarburization-whitening chamber and a heating chamber. Although electric heating of the heating chamber is also feasible, it is best from the economic point of view to use kerosene or heavy oil for combustion. The hot air obtained by recovering the above-mentioned volatile gas from the mud and burning it can also be used. In addition, the combustion gas discharged from other existing incineration equipment such as an incinerator can also be used. The type of incineration equipment can be exemplified by the furnace type (such as the type of stoker furnace), the floating type, the material stirring type, and the hot air combustion type. 'In addition, a rotary kiln installed in each papermaking plant or an existing incinerator (cyclonic furnace or mobile incinerator) can be used as a part of the wastewater treatment device', and it is even better to use a Rotary kiln for decarbonization and albino treatment. In addition, during the carbonization treatment and decarburization-whitening treatment, once the object to be treated is cooled to a temperature of 400 ° C or lower, and then the subsequent treatment is performed, the carbide can be completely removed due to the carbonization treatment. Combustible gas from thermal decomposition of organic matter. In addition, when the carbide is brought into contact with water and / or water vapor for cooling during this period, the specific surface area of the carbide can be increased, and the reaction efficiency between the treated product and oxygen in the decarburization-whitening treatment step can be effectively increased. Decarbonization-whitening treatment. In the case of continuous carbonization and decarbonization-whitening, when a screw or a stirring blade is installed in the heat treatment chamber, sludge or carbide can be forcibly transferred by this. When forcibly squeezed in with a screw, stirring can be promoted to improve the efficiency of concrete treatment.
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527455 發明說明(16) :使多角形之碳化室旋轉時,亦可藉此移送游泥或碳 (粉碎步驟) m 關方、白色無機粒子之粉碎步驟5 4加以說明。經過 造紙用之粒徑。最適\色無機粒子可予以調節其適於 . 取適粒樘乃依使用方法而不同,不過,約 略以〇 · 1 // m〜1 〇 // m為較私々如_ 山 卜V 、习 嬙私工 > 认/ f ^土之粒役。脫碳-白化後之白色盔 ί;:;輸送至乾式粉碎機,以經過-次粉碎。一^ i 後之粉體被移送至分散 ¥ 认叔碎 拌而漿體化。錢,此漿 ^或父$之分散劑-起被 體經過二次粉碎,_ ; 式粉碎機,以使粉 為粉碎方法,僅利白色無機粒子)。 碎機之粉碎均有可行性,c式叔碎機之粉碎或僅利用濕式粉 粉碎機與濕式粉碎機之適佳的* ’如上所述,乾式 別或僅一方設置複數# 、 σ 亦有可能在各粉碎機各 後可成為適於造紙之‘值無機粒子之平均粒徑在最 上更佳的是,在濕式粉=式施行粉碎,而在粉碎效率 象物小粒化。此時,經屬:二預先藉乾式粉碎使處理對 3 5 // m,分散機内之粉體1〜之^粉碎t後之粉體之粒徑若超過 之粉碎效率惡化之同時版,八散狀態則會惡化,使粉碎機 色無機粒子之白色度^低刀放機或粉碎機被磨耗,而使白 ΪΪ22❹以下;會得ί4乾式粉碎時,若將粉 上不合適。 民之粉碎效率,而在經濟 f栈組合之下,藉乾式粉527455 Description of the invention (16): When rotating the polygonal carbonization chamber, you can also use this to transfer mud or carbon (grinding step) m Guanfang, white inorganic particle crushing step 5 4 will be described. Particle size for papermaking. The most suitable / colored inorganic particles can be adjusted to suit their suitability. Taking suitable granules depends on the method of use, but it is slightly more private such as 〇 · 1 // m ~ 1 〇 // m, such as _ 山 卜 V 、 习 嫱Private Worker > Recognition / f ^ Granule of Earth. Decarburization-whitening helmet ί;:; Conveyed to a dry grinder for pulverization. The powder after one ^ i is transferred to the dispersion. The pulverizer, or the dispersant of the slurry, is subjected to secondary pulverization, and the pulverizer is a pulverizer, so that the powder is a pulverization method, which only benefits white inorganic particles). The crushing of the crusher is feasible. The crushing of the C-type tertiary crusher or the wet powder crusher and the wet crusher are only suitable. * As mentioned above, the dry type or only one side is provided with a plurality of # and σ. It is possible that the average particle size of the inorganic particles that can be made into a suitable value for papermaking after each of the pulverizers is most preferably that the pulverization is performed in a wet powder type, and the pulverization efficiency is small. At this time, the warfare belongs to the following: the dry powder pulverization in advance makes the treatment pair 3 5 // m, the powder in the dispersing machine 1 ~ ^^ after the powder particle size after pulverization t exceeds the simultaneous deterioration of the crushing efficiency, the The state will worsen, making the whiteness of the pulverizer-colored inorganic particles ^ low-knife or pulverizer abrasion, and making the white kiln less than 22 会; when dry dry pulverization, if powder is not suitable. People's crushing efficiency, and under the economic f stack combination, borrow dry powder
C.\2D-CODE\90-11\9〇117420.ptd $ 21頁 因此’在乾式粉碎機與 五、發明說明(17) 碎予以粉碎以達到粒體 10 一更佳,而予以二粉=r:35 形分即固形物含量(例如5 ::::有所指定之固 -邊防止由分散機或湯式粉)之水性漿體時,可藉此 降低’ -邊以良好之效率粉 :耗:引起之白色度之 ,之白色無機粒子之平均粒徑可達到此日守,以濕式粉碎 式予以粉碎即可。若其粉碎程;〜10 _之方 在加工時發生報子表面之磨,=二,求,則在造紙時或 刃,造成嚴重之問題。因,_ 頌著磨耗切割機之刀 調節為0· 1 "m〜10心時,可將白色無機粒子之平均粒徑 子之磨耗性。 9 文。造紙用白色無機粒 以下關於乾式粉碎冑, 粉碎至數十之粉碎機, 4、,、田之說明。為可從數_ 碾機、刀磨機、桿磨機等。彳不輥壓碎機、輥磨機、輪 之數// m以下之大小者,為可實現適於造紙原料 射式磨機、乾式球磨機::碎機,可使用滾磨機、噴 乾式粉碎機之材質使】5粉碎機等。又按,為此等 其次’為濕式粉碎機,:::,已做過磨耗上之考慮。 機、攪拌槽型磨機、、此使用濕式球磨機、振動磨 碎機)等,以施行、、蟲 、g型磨機、⑶BALL-MILL(超微粉 磨耗所引起之白色、益"&碎。此外,為了防止由粉碎機之 的是,使粉碎機之救;碎=子=污染(白色度之降低),較佳 磨性塑膠等。所提=平=被覆有耐磨性材料例如橡膠、耐 件之外表面而言,在碎區乃指粉碎室内表面及攪拌構 ° ,、匕括粉碎時之漿液(漿體)中之粉體所 C:\2D-OODE\90-ll\90117420.ptd 第22頁 527455 五、發明說明(18) 接觸之區域。在粉碎室設有隔板等之構件之場合,此等構 件亦成為粉碎區之一部分。又按,在使用磨球等之類為粉 碎媒肢之濕式粉碎機之情況,最好能使用被覆有耐磨性塑 膠之磨球或陶瓷製之磨球,而此等磨球亦成為粉碎區之一 ,分。為耐磨性塑膠,可例示胺曱酸酯樹脂或耐綸樹脂, 最好能按大約1 mm〜1 〇_程度之厚度施加被覆,而可依照 使用頻度或粉碎條件予以適當選擇。又按,亦可以在濕式 粉碎之前後,藉由篩選裝置(如開放型振動篩、多管式振 動加疋;慮為、機械式加壓滤器等)除去難粉碎性之燒結 物。再者,對前述之分散機亦最好能使其分散區以與濕式 赤刀碎機相同之方式被覆有橡膠、耐磨性塑膠等之類。 在濕式粉碎之際,在粉體之均勻分散為目的之下,添加 分散劑以施行漿體化。在添加有分散劑時,可藉此防止黏 度之上升,即使在漿液被高濃度化時亦然,此外,可防止 由濕式粉碎所引起之黏度之上升,而提高粉碎效率或運用 =。此時,為了使含有磺酸基之聚丙烯酸之分散劑具有比 其他分散劑為優之耐鹽性及耐熱性為其優點,最好能添加 一含有項酸基之聚丙稀酸(其包括磺酸基在内之分子量例 士口為1 0 0 0 〜 1 0 0 0 0 ) 0·05%〜以作為分散劑。在該添加量 超過3%時,即使增加添加量,其分散性亦不會改盖,而若 該添加量為0·05%以下,則顯示不良之分散性,無ϋ法以良 好之效率施行其後步驟之濕式粉碎。步驟55所示者為經過 粉碎處理被調節粒徑後之白色無機粒子,(由於如此處理) 有可能被重複利用以作為適於造紙之顏料或填料。C. \ 2D-CODE \ 90-11 \ 9〇117420.ptd $ 21 pages. So 'in the dry grinder and V. Description of the invention (17) Crushing and crushing to achieve a granular 10, better, and two powders = r: 35 form is the solid content (such as 5 :::: specified solid-edge prevention by the disperser or soup powder) of the aqueous slurry, which can be used to reduce the '-edge with good efficiency powder : Consumption: Caused by the whiteness, the average particle size of the white inorganic particles can reach this date, and it can be pulverized by wet pulverization. If its pulverization process; ~ 10 _ square grinding of the surface of the newspaper occurs during processing, = two, demand, it will cause serious problems during papermaking. The reason is that when the blade of the abrasive cutting machine is adjusted to 0 · 1 " m ~ 10 cores, the average particle size of the white inorganic particles can be worn. 9 texts. White inorganic granules for papermaking The following is a description of a dry pulverizer, a pulverizer that pulverizes to several tens of mills. It is available from the number of mills, knife mills, rod mills, etc.彳 No roll crusher, roll mill, wheel size below // m, in order to realize the jet mill, dry ball mill suitable for papermaking raw materials :: crusher, roll mill, spray dry crushing can be used The material of the machine is 5 grinder and so on. Press again, and so on. Secondly, the “wet grinder” ::: has been considered for abrasion. Machine, mixing tank type mill, wet ball mill, vibrating mill), etc., to implement, worm, g-type mill, ⑶BALL-MILL (white caused by ultrafine powder wear, benefit " & In addition, in order to prevent the crusher from being rescued by the crusher; broken = sub = pollution (reduction in whiteness), preferably abrasive plastic, etc. mentioned = flat = coated with abrasion-resistant materials such as In terms of the outer surface of rubber and durable parts, the crushing area refers to the surface of the crushing chamber and the stirring structure, and the powder in the slurry (slurry) during crushing C: \ 2D-OODE \ 90-ll \ 90117420.ptd Page 22 527455 V. Description of the invention (18) Contact area. When the crushing chamber is provided with partitions and other components, these components also become part of the crushing area. For the case of wet grinders that crush media limbs, it is best to use abrasive balls covered with abrasion-resistant plastic or ceramic balls, and these balls also become one of the crushing areas. Plastics, such as urethane resin or nylon resin, can be exemplified by a thickness of about 1 mm to 1 〇_ The coating can be applied, and it can be appropriately selected according to the frequency of use or the pulverizing conditions. Press again, and you can also use a screening device (such as an open-type vibrating screen, multi-tubular vibration vibrating filter) before and after wet pulverization; (Pressure filter, etc.) to remove sintered materials that are difficult to crush. Furthermore, it is preferable that the dispersing machine be coated with rubber, wear-resistant plastic, etc. in the same manner as the wet red knife crusher. In the case of wet pulverization, under the purpose of uniform powder dispersion, a dispersant is added to perform slurrying. When a dispersant is added, it can prevent the viscosity from increasing, even when the slurry is highly concentrated. It is also the same when changing, in addition, it can prevent the viscosity increase caused by wet pulverization, and improve the pulverization efficiency or use =. At this time, in order to make the dispersant of polyacrylic acid containing sulfonic acid group have better than other dispersants The salt resistance and heat resistance are its advantages. It is best to add a polyacrylic acid containing an acid group (its molecular weight including the sulfonic acid group is 1 0 0 0 to 1 0 0 0 0) 0 05% to as a dispersant. When the added amount exceeds 3%, even if the added amount is increased, its dispersibility will not be changed. If the added amount is less than 0.05%, it will show poor dispersibility, and there is no way to perform it with good efficiency. Wet pulverization in step. The one shown in step 55 is white inorganic particles whose particle size is adjusted after pulverization treatment (due to this treatment), which may be reused as a pigment or filler suitable for papermaking.
C:\2D^DE\9〇.li\9〇i17420.ptd 527455 五、發明說明(19) 生H=稀釋白色無機粒子懸浮液之際,若懸浮 液顯不具pH大於1 3之鹼性,丨畀 t 13。此項調整之理^ 酸來調整pH為8〜 1 , 由為,在懸浮液之PH高時,分散劑之效 果則降低,而使粉碎性痞、、六 刀威d义 >艾 >義為含有尤^ ^次⑽動性降低。又按,水性媒體之 機粒::懸浮液最好能使 二二白色… 子之產率。在白色無機Π :J高白色無機粒C: \ 2D ^ DE \ 9〇.li \ 9〇i17420.ptd 527455 V. Description of the invention (19) When H = diluted white inorganic particle suspension, if the suspension is not alkaline with pH greater than 13,丨 畀 t 13. The reason for this adjustment is to adjust the pH to 8 ~ 1 with an acid, so that when the pH of the suspension is high, the effect of the dispersant is reduced, and the pulverizability is reduced. This means that it contains especially ^^ times of reduced mobility. Press again, the organic granules of the aqueous media :: The suspension should make the yield of 22 white ... In white inorganic Π: J high white inorganic particles
時,可藉此實現防止點度上升IS效;:處理之前調整PH 反之,在白色無機粒子懸浮液之pH調 機粒子之平均粒徑調節 之則’將白色無 有效調整。此外,亦;下時,可藉此實現PH之 際,施行二氧化碳嶋粒子之分散、粉碎之 pH處理。調整pH後之含右^ 错此同時進行分散處理及 式粉碎、儲存、輪送彳纟# :機粒子之懸浮液可經過濕 又按,如上所述紙用之原料。 化時,可視為已進入使=二=7以使白色無機粒子漿體 段。 使用白色無機粒子為顏料或填料之階 當然,亦可以將白儿士 m ^ 不予以乾式粉碎或濕式二:::::;;白色無機粒子 合等广,用水性::來色;2:::=之原料之場 多。在此項稀釋之際, 色…栈粒子之情況較In this way, it is possible to achieve the IS effect to prevent the dots from rising; adjust the pH before processing; otherwise, adjust the average particle diameter of the pH-adjusted particles of the white inorganic particle suspension ’to effectively adjust the white color. In addition, at the following time, when pH can be achieved, the pH treatment of carbon dioxide and particles is dispersed and pulverized. After adjusting the pH, it contains the right and wrong. At the same time, the dispersion treatment and crushing, storage, and rotation are performed at the same time. #: The suspension of machine particles can be wet and pressed. At the time of conversion, it can be regarded as having entered = 2 = 7 to make the white inorganic particle slurry segment. The use of white inorganic particles as pigments or fillers Of course, white children m ^ can not be dry pulverized or wet type 2 ::::: ;; white inorganic particles are broad, water-based :: color; 2 ::: = There are many raw materials. At the time of this dilution, the color ...
為8〜13。在此種場合亦更佳的"V用酸來/周整懸浮液之pH 、疋,用一氧化碳來調整懸 C:\2D-O0DE\90·1]\90117420.ptd 第24頁 527455 五、發明說明(20) 浮液之pH為8〜13。在使白色無機粒子分 化破導入時。可藉此同時進行分散處理及"調整。 茲關於本發明之方法中使用之熱處理裝置之一例,在參 照圖2之下加以詳細說明。圖2為施行本發明之碳化步驟及 脫碳-白化處理步驟之熱處理裝置—例之概略系統圖。 泥彳之弟間接加熱爐之於泥投入口 2投入,而在於泥乾燥 室3予以乾°為了於泥乾燥室之加熱,設有熱風進入口 4a,暨熱風、水蒸氣、以及乾餾氣體之排出口 5a。又按, 在排出口 5 a近旁有微小開口部(省略圖示)被設在於泥乾燥 室3之後半部分’以便將從於泥產生之水蒸氣等之類排出 於該排出口。 碳化步驟係用第-間接加熱⑴及第二間接加熱爐6來進 行者。脫碳-白化處理步驟係用第三間接加熱爐1〇來進行 者。第一間接加熱爐1係屬於碳化步驟之乾燥帶,以將淤 第二間接加熱爐6乃屬於碳化步驟之熱分解帶。在第二 間接加熱爐6之淤泥熱分解及碳化室7之一方設有熱風(被 用於以乾燥淤泥之碳化為目的之加熱室之加熱)進入口 4 b,而在另一方設有熱風、水蒸氣、以及乾餾氣體之排出 口 5b。又按,在排出口 5b近旁有微小開口部(省略圖示)被 ό又在於泥熱为解及石反化室7之後半部分’以便將從於泥產 生之乾餾氣體等之類排出於該排出口。當碳化終了時,碳 化物則從碳化物排出口 8被排出去。 Κ 從碳化物排出口 8排出之碳化物乃藉由碳化物移送流路9 被送入第三間接加熱爐1 〇,以施加脫碳—白化處理。在第It is 8 to 13. It is also better in this case. "V is used to adjust the pH and pH of the suspension, and carbon monoxide is used to adjust the suspension C: \ 2D-O0DE \ 90 · 1] \ 90117420.ptd Page 24 527455 5. Description of the invention (20) The pH of the floating liquid is 8-13. When introducing and separating white inorganic particles. This allows simultaneous decentralization and " adjustment. An example of the heat treatment apparatus used in the method of the present invention is described in detail below with reference to FIG. 2. FIG. 2 is a schematic system diagram of an example of a heat treatment device that performs the carbonization step and the decarburization-whitening treatment step of the present invention. The indirect heating furnace of the loach is put in the mud input port 2 and dried in the mud drying chamber 3 ° In order to heat the mud drying chamber, a hot air inlet 4a is provided, and the exhaust of hot air, water vapor, and dry distillation gas is provided. Exit 5a. Further, a minute opening (not shown) is provided near the discharge port 5a at the rear half of the mud drying chamber 3 'so as to discharge water vapor or the like generated from the mud to the discharge port. The carbonization step is performed by using the first-indirect heating furnace and the second indirect heating furnace 6. The decarburization-whitening treatment step is performed using a third indirect heating furnace 10. The first indirect heating furnace 1 is a drying zone belonging to the carbonization step, and the second indirect heating furnace 6 is a thermal decomposition zone belonging to the carbonization step. One of the sludge thermal decomposition and carbonization chambers 7 of the second indirect heating furnace 6 is provided with a hot air inlet (used to heat the heating chamber for the purpose of drying the carbonization of the sludge). The inlet 4 b is provided, and the other side is provided with hot air, The outlet 5b of water vapor and dry distillation gas. Also, there is a small opening (not shown) near the discharge port 5b. The mud heat is decomposed and the second half of the stone reaction chamber 7 is' in order to discharge the dry distillation gas and the like generated from the mud. Exhaust. When the carbonization is completed, the carbide is discharged from the carbide discharge port 8. The carbide discharged from the carbide discharge port 8 is sent to the third indirect heating furnace 10 through the carbide transfer flow path 9 to apply a decarburization-whitening treatment. In the
C:\2D-CODE\90-ll\90117420.ptd 第25頁 527455C: \ 2D-CODE \ 90-ll \ 90117420.ptd Page 25 527455
52^455 五、發明說明(22) 、氣體亦發生燃燒,而可用作淤泥之乾燥、唆化 。將碳化室7之溫度設定為4〇〇 °C〜1 0 0 0 °C(以^ ,熱源。 C較佳)時,可藉此在不發生淤泥所含白色盔 C〜700 ,,望之熱變性之溫度下,促進有機物之熱分4解姐。子之不 等溫度’可用熱風產生裝置來調節所產生、=。關於此 供认旦 *、、、風之择 〜里、以及排出量。 、/皿度、 在連續進行碳化及脫壤-白化之場合,在熱卢 有螺桿或攪拌葉片時,可藉此強制移送淤、处理室内設 π V) ^ ^ 、’匕。、/於泥之机 係以空氣不致被帶入碳化室之方式設成最 匕 < 投入 之開口。藉攪拌葉片強制擠入時,可限制所往Z度所需要 再者,由利用螺旋來促進淤泥之授拌, ^ ^ 率。 可提高熱效 後化時間係可藉一種在使用氣體檢知裝置之 ^ 分解所產生之可燃氣體量之方法來調節者。下’則定由熱 4曰〜 百此際,钿扭 干之旋轉速度即可調節於泥之滯留時間。圖2 —㈣正螺 段施行碳化步驟之例子,不過亦有可能 不Μ二階 理。亦有可能使用二軸式之螺桿,以便一邊 ^之處 ,一邊使之碳化。雖然有機物由來之碳與碳酸 ^ 石反難於區別,不過較佳的是,以最後可令 、’3由來之 被固定碳化及碳酸鈣由來碳保持碳酸鈣之由來之碳 理。 )又方式施行碳化處 、、彳關於圖2,說明脫碳-白化處理步驟。將藉由 迗k路9送過來之碳化物從設在第三間接加熱爐丨〇之勿矛夕 口 11投入。此際,可將碳化物之碳化所需要之空氣從又空氣52 ^ 455 5. Description of the invention (22) The gas also burns and can be used for drying and trituration of sludge. When the temperature of the carbonization chamber 7 is set to 400 ° C ~ 100 ° C (with ^, the heat source is preferably C), the white helmet C ~ 700 contained in the silt can be avoided by this. At the temperature of thermal denaturation, it promotes the thermal decomposition of organic matter. The unequal temperature of the child can be adjusted by the hot air generating device. Regarding this, it is acknowledged that *, ,, wind choices ~ miles, and emissions. In the case of continuous carbonization and desalting-whitening, when there is a screw or agitating blades in Relu, it can be used to forcibly transfer the silt, and π V) ^ ^ ^ 、 / The machine for mud is set as the opening for the most dagger < so that the air will not be taken into the carbonization chamber. When forced in by the stirring blades, it is possible to limit the Z-direction required. Furthermore, the use of spirals to promote the sludge mixing, ^ ^ rate. Improved thermal efficiency The post-chemical time can be adjusted by a method that uses the amount of combustible gas produced by the decomposition of a gas detection device. The next time is determined by the heat. The rotation speed can be adjusted to the residence time of the mud. Figure 2-An example of the carbonization step in the snail section, but it is also possible to use the second-order principle. It is also possible to use a two-axis screw in order to carbonize it at the same time. Although the carbon derived from organic matter is difficult to distinguish from carbonic acid, it is better to keep the carbon derived from calcium carbonate by fixing carbonization and carbon dioxide derived from calcium carbonate. ) Another way to implement the carbonization section, and 彳 With reference to Figure 2, the decarbonization-whitening process steps will be described. The carbide delivered through 迗 k 路 9 was put in from the No. 11 port set in the third indirect heating furnace. At this time, the air required for the carbonization of the carbide can be removed from the air
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527455 五、發明說明(24) t例為利用 例。將碳化物 燃式旋窯之碳 處理室1 8、燃 由碳化步驟 處理步驟,而 將碳化物一旦 為了増加碳化 藉果加壓之水 之噴霧處理。 體噴嘴時,可 能實現更均勻 其次,關於 說明。 内燃式旋窯15來施行脫碳—白化 一旦儲存於碳化物 处里之一 化物投入口 d器16内之後’再從内 燒哭1 9、以及& & 亥窯设有脫碳、白化 U及白色無機粒 所得到之竣化物並未直接移送:2;。 予以儲存於儲存器16 ,反-白化 冷部,以使可燃氣體完全揮 ^彳土 6疋, 物之比表面積,亦有可#,t ΐ去。此外, W』月b施灯水之哈费 使用噴霧喷嘴予以噴# 贺務。將 使用一種可將水及加壓空氣同時噴射之二 藉此調節水粒之大小為loop以下,而:= 之喷霧處理。 而有可 在脫碳-白化處理步驟使用旋熏之步驟加以 攸内燃式旋窯1 5之碳化物投入口 J 7沪 要从, 〖奴入之碳化物乃套 置於白色無機粒子回收口 20附近之燃燒器19予以=寿· 熱。以爐内溫度可達到450 t〜1 0 0 0 t範圍内之⑺按力 予以加熱時,可藉此有效提高白色度。此際,車^皿佳夂万^ 以碳化物不致被急劇加熱之方式調節對燃燒器19供仏^ 料,以調節爐内溫度。 °527455 V. Description of the invention (24) t example is a use example. Carburize the carbon in the rotary kiln's carbon treatment chamber 18. Combustion is performed by the carbonization step, and once the carbide is sprayed for the purpose of adding carbonized water to the pressurized water. It is possible to achieve a more uniform body nozzle. Second, about the description. Internal combustion-type rotary kiln 15 for decarbonization-whitening Once stored in the carbide, one of the compounds is placed in the port 16 and then burned from the inside 19, and & & The kiln is equipped with decarbonization and whitening The finished compounds obtained from U and white inorganic particles were not directly transferred: 2 ;. It is stored in the storage 16 and the anti-whitening cold part, so that the flammable gas is completely evaporated, and the specific surface area of the material can also be removed. In addition, Harley-Davidson's use of spray water is sprayed using a spray nozzle. Will use a spray of water and pressurized air at the same time to adjust the size of the water particles below the loop, and: = spray treatment. In the decarburization-whitening treatment step, the spin-fumbling step can be used to add the carbide inlet 15 of the internal combustion rotary kiln J 7 and the slag to be placed in the white inorganic particle recovery port 20 The nearby burner 19 gives life and heat. When the heating temperature is within the range of 450 t ~ 100 0 t, the whiteness can be effectively improved. At this time, the vehicle is adjusted in such a way that the carbide is not heated sharply so as to adjust the temperature of the furnace. °
最好能使脫碳-白化處理18之内壁形狀形成多角形,藉 此,除了可連續移送碳化物之外,亦可攪拌碳化物,而曰可 有效施行脫碳及白化處理。調節旋窯15之轉數及傾角即可 谷易S周節脫碳-白化處理時間。依此處理時間可製造適於It is desirable that the inner wall shape of the decarburization-whitening treatment 18 can be formed into a polygonal shape, so that in addition to the continuous transfer of carbides, the carbides can be stirred, and the decarburization and whitening treatment can be effectively performed. Adjusting the number of revolutions and the inclination of the rotary kiln 15 can be used for the decarburization-whitening treatment time. Based on this processing time, suitable for manufacturing
527455 五、發明說明(25) 造紙用原料之白色無機粒子。最後,可將白色無機粒子之 白色度調整為70%以上,以80%以上較佳。又按,對於從内 燃式旋寞1 5排出之燃燒氣體,最好能用一廢氣處理裝置 (省略圖示)予以處理。 雖然在圖3中使用碳化物儲存器1 6,但亦有可行性的是 ’用碳化物移送流路9來直接連接碳化處理步驟之間接加 熱爐與脫碳-白化處理步驟之旋窯。再者,在圖2中,亦有 可能使用碳化物儲存器1 6來代替碳化物移送流路9。 ^ 除了圖3中所用之内燃式旋窯之外,亦可使用現有之焚 燒爐(旋風爐或流動床焚燒爐),其以排水處理裝置之一部 分被設在各造紙工場者。亦可以使用間接加熱式之旋窯,彳_ 而為熱風,有可能使用從現有之焚燒設備如焚燒爐等排出 之燃燒氣體。尤其較佳的是,在竣化處理裝置及脫碳-白 化裝置使用斷熱材料,對周圍施加被覆以保溫此等裝置。 再者,為此等裝置之材質,在考慮處理溫度或經濟性之 下,可選擇陶瓷或合金類。 如此處理造紙淤泥而得到之材料乃在外觀上呈白色系之 顏色。尤其具有可再循環之處理方法上之特徵及經過該處 理所得之材料上之特徵。由如此處理造紙淤泥等所得到之 材料可在用途上以碳酸鈣或高嶺土再被利用以作為上質紙 等之造紙過程中之紙漿懸浮液之調質材。再者,若將此項 材料加入有色混濁水或茶等之水溶液,則會吸附色素等而 使水溶液之顏色變淡,又會吸附香煙之煙,因此證實該材 料為具有多孔性之活性物質。由於殘存有多孔性,亦可被527455 V. Description of the invention (25) White inorganic particles of papermaking raw materials. Finally, the whiteness of the white inorganic particles can be adjusted to 70% or more, preferably 80% or more. Also, it is preferable that the combustion gas exhausted from the internal combustion-type rotary vane 15 can be treated by an exhaust gas treatment device (not shown). Although the carbide reservoir 16 is used in FIG. 3, it is also feasible to use a carbide transfer flow path 9 to directly connect the rotary kiln between the carbonization treatment step heating furnace and the decarburization-whitening treatment step. In addition, in FIG. 2, it is also possible to use a carbide reservoir 16 instead of the carbide transfer flow path 9. ^ In addition to the internal combustion type rotary kiln used in Figure 3, existing incinerators (cyclone furnaces or fluid bed incinerators) can also be used, which are installed in each paper mill as part of a drainage treatment plant. It is also possible to use an indirect heating type rotary kiln. For hot air, it is possible to use combustion gases exhausted from existing incineration equipment such as incinerators. It is particularly preferable to use a heat-insulating material in the finishing treatment device and the decarburization-whitening device, and apply a coating to the surroundings to keep these devices warm. Furthermore, ceramics or alloys can be selected as the material of these devices, taking into consideration the processing temperature or economy. The material obtained by treating the papermaking sludge in this way is white in appearance. In particular, it has the characteristics of a recyclable processing method and the characteristics of the materials obtained through the processing. The material obtained by treating papermaking sludge and the like in this way can be reused as calcium carbonate or kaolin for use as a tempering material for a pulp suspension in a papermaking process such as high-quality paper. Furthermore, if this material is added to an aqueous solution of colored turbid water or tea, it will adsorb pigments and make the color of the aqueous solution lighter, and it will adsorb cigarette smoke. Therefore, it is confirmed that the material is a porous active substance. Due to the residual porosity, it can also be
C:\2D-C0DE\90-ll\90117420.ptd 第30頁 527455 五、發明說明(26) [利/二Γ污泥處理上之活性菌、細菌之培養載體等。 以下敘述實施例,以進一步具體說明本發明。又 發明並未受到此等實施例之限制,因為在目的、 本 及产果上與本發明實質相同* 於本 5、以 (實施例1 ) 乾可。 對於由一具有脫墨紙漿(用作洋紙之原料)化設 器所分離之固形物所構成之於泥,用脫水= 固形物 >辰度可達到約50%之方式施加脫水處理。 淤泥之乾紐處理係在使用一種窯型之間接加熱焯 (”Adva'tec東洋’,公司製品)之下施行者。將按每^鐘?轉 之速度旋轉之石英製之小型窯之周圍藉電熱線予以間接加 熱,而閉塞此窯之試料投入口,以防空氣流入。將水蒸氣 及乾餾氣體從另一方之開放口排出。關於碳化溫度,按前 半之30分鐘使窯内氣氛溫度達到4 0 0。(3之速度施行加熱。 在於泥之乾燥後,利用上述之旋窯來施行熱分解及碳化 處理。按30分鐘之時間達到6〇〇 π之速度施行加熱。 其次’利用此一小型窯,以6 〇分鐘之時間加熱至6 〇 0 C ’將空氣按每分鐘50Occ之速率供給於充當脫碳-白化室 之寞内以施行所得碳化物之脫碳-白化處理,而回收試料 (試驗產物,以下皆同)。 (實施例2 ) 在實施例2中,除了將脫碳-白化處理步驟中之最高到達 溫度設定為8 0 0 °C之外,均施行與實施例1相同之處理。在C: \ 2D-C0DE \ 90-ll \ 90117420.ptd Page 30 527455 V. Description of the invention (26) [Li / Er Γ Active bacteria on sludge treatment, bacterial culture carrier, etc. The examples are described below to further illustrate the present invention. The invention is not limited by these examples, because it is substantially the same as the present invention in terms of purpose, cost, and fruit. * In this example, (Example 1) may be used. For the sludge composed of solids separated by a deinking pulp (used as a raw material for foreign paper), the dewatering treatment is applied in such a way that the dehydration = solids can reach about 50%. The sludge treatment is performed under the use of a kiln type indirect heating slab ("Adva'tec Toyo", a product of the company). It will be borrowed around a small kiln made of quartz that will rotate at a speed of ^ clock? The electric heating wire indirectly heats it, and blocks the sample input port of the kiln to prevent air from flowing in. The water vapor and carbonized gas are discharged from the open port of the other side. Regarding the carbonization temperature, the temperature of the atmosphere in the kiln reaches 4 in the first 30 minutes. 0 0. (The heating is performed at a rate of 3. After the mud is dried, the above-mentioned rotary kiln is used to perform thermal decomposition and carbonization. The heating is performed at a speed of 60 π in 30 minutes. Second, 'use this small Kiln, heating to 600 C in 60 minutes' time, supplying air at a rate of 50Occ per minute into a lonely chamber serving as a decarburization-whitening chamber to perform decarburization-whitening treatment of the obtained carbide, and recovering the sample ( The test products are the same below.) (Example 2) In Example 2, the same procedure as in Example 1 was performed except that the highest temperature reached in the decarburization-whitening treatment step was set to 80 ° C. deal with In
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C:\2D-C0DE\90·11\90117420.ptd 第33頁 527455 五、發明說明(29) 表1 碳化溫度 (°C) 水蒸氣 噴霧 脱碳溫度 (°C) 高嶺土 /碳酸鈣 之X射線繞射 白色無機粒子 之白色度(%) 塗層紙之 白色度(%) 實施例1 400-600 無 600 100/2500 72 74 實施例2 // // 500—800 無/無 86 82 實施例3 // 有 600 100/2500 75 78 實施例4 // 無 580-700 無/1300 85 82 比較例1 無^ 無 800—800 無/500 72 74 比較例2 400—600 // 1200 無/無 74 無法粉碎 比較例3 無 無 焚燒爐 無/無 54 64 比較例4 現有之製品:“hy(irocurve -90”(乾式重質碳酸鈣) 96 86 現有之製品:HT(2級高嶺土) 78 79 在實施例1所得之試料之X射線繞射(圖)中,明確顯示碳 酸約之尖峰,而由於經過脫碳-白化處理,淤泥中之白色 無機粒子之變化很少。此外,試料之白色度為7 2 %之高 值,如此適於被用作造紙原料,即確認碳化處理〜脫碳一 白化處理步驟之效果。 在實施例2所得之試料之X射線繞射(圖)中,並未觀察到 高嶺土或碳酸#5之尖峰,但試樣之白色度高達8 6 %,即確 認在8 0 0 °C溫度下所行之脫碳-白化處理之效果。 實施例3所得之試料之X射線繞射之結果與實施例1之粒 子之測定值約略相等,此外,所回收之試料之白色度為 75%,高於實施例1,亦即適於被用作造紙原料。為此可推C: \ 2D-C0DE \ 90 · 11 \ 90117420.ptd Page 33 527455 V. Description of the invention (29) Table 1 Carbonization temperature (° C) Water vapor spray decarburization temperature (° C) X-ray of kaolin / calcium carbonate Whiteness (%) of diffractive white inorganic particles Whiteness (%) of coated paper Example 1 400-600 No 600 100/2500 72 74 Example 2 // // 500-800 No / No 86 82 Example 3 // Yes 600 100/2500 75 78 Example 4 // None 580-700 None / 1300 85 82 Comparative Example 1 None ^ None 800-800 None / 500 72 74 Comparative Example 2 400-600 // 1200 None / None 74 Uncomparable Comparative Example 3 None No incinerator None / No 54 64 Comparative Example 4 Existing product: "hy (irocurve -90" (dry heavy calcium carbonate) 96 86 Existing product: HT (grade 2 kaolin) 78 79 In the X-ray diffraction (picture) of the sample obtained in Example 1, the sharp peak of carbonic acid is clearly shown, and the white inorganic particles in the sludge have little change due to the decarbonization-whitening treatment. In addition, the whiteness of the sample It is a high value of 72%, so it is suitable for being used as a raw material for papermaking, that is, the effect of the carbonization treatment ~ decarburization-whitening treatment step is confirmed. In the X-ray diffraction (picture) of the sample obtained in Example 2, no spike of kaolin or carbonic acid # 5 was observed, but the whiteness of the sample was as high as 86%, that is, it was confirmed that the sample was at 80 ° C. The effect of the decarburization-whitening treatment was performed. The X-ray diffraction results of the sample obtained in Example 3 were approximately equal to the measured values of the particles of Example 1. In addition, the whiteness of the recovered sample was 75%, which was higher than Example 1 is suitable for being used as a raw material for papermaking.
C:\2D-CODE\90-ll\90117420.ptd 第 34 頁 527455 五、發明說明(30) 斷的是,由於對碳化物施行用水之喷霧處理,碳化物之比 表面積增加,致使碳化物與氧氣有效接觸,於是被脫碳而 白化。即確認水之喷霧效果。 在實施例4所得之試料之X射線繞射(圖)中,明確顯示碳 酸鈣之尖峰,並且所回收之試料之白色度為8 5 %,即與實 施例2相等,如此適於被用作造紙原料。由於在白化處理 步驟中採取一種在6 0 0 °C以下之溫度下充分脫碳後在7 〇 〇 t 溫度下施行二階段烺燒之方法以及施行空氣流量之調整, 可在防止石反3文I弓之分解及白色無機粒子之熱變性之下提高C: \ 2D-CODE \ 90-ll \ 90117420.ptd page 34 527455 V. Description of the invention (30) It is concluded that the specific surface area of carbides is increased due to the spraying treatment of water on the carbides, resulting in carbides Effectively in contact with oxygen, it is decarburized and whitened. That is, the spray effect of water was confirmed. In the X-ray diffraction (picture) of the sample obtained in Example 4, the peak of calcium carbonate is clearly displayed, and the whiteness of the recovered sample is 85%, which is equivalent to that in Example 2, so it is suitable for use as Papermaking raw materials. In the whitening treatment step, a method of performing two-stage sintering at a temperature of 7000t after full decarburization at a temperature below 600 ° C and an adjustment of air flow can be used to prevent stone reflection. Decomposition of I bow and thermal degradation of white inorganic particles
在比較例1所得之試料之χ射線繞射(圖)中,並未明確顯 不高嶺土及碳酸鈣之尖峰,而試料之白色度為7 2 g/g。雖然 在比實施例1為咼之8 0 〇 °c溫度下施行熱處理淤泥,但所得 到之白色度卻與實施例1相等。為其脫碳—白化效率降低: 原因,可推斷的是,由於不經過碳化步驟之淤泥之急劇熱 處理,引起淤泥所含之白色無機粒子發生在造紙上不二 之熔融·燒結所致。 σ 在比較例2所得之試料之X射線繞射(圖)中,並無高嶺土 及碳酸鈣之尖峰。所回收之試料之白色度為74%。由於脫 碳-白化處理中之急劇熱處理而發生淤泥所含之白色無 粒子之溶融·燒結’致使白色度之提高率降低。 在比較例3所得之試料之χ射線繞射(圖)中,並無高 及碳酸鈣之尖峰。焚燒灰之白色度為54%,即很低,\ 於造紙原料。 ^In the X-ray diffraction (picture) of the sample obtained in Comparative Example 1, the peaks of kaolin and calcium carbonate were not clearly shown, and the whiteness of the sample was 7 2 g / g. Although the sludge was heat-treated at a temperature of 800 ° C, which is higher than that of Example 1, the obtained whiteness was equal to that of Example 1. The decarburization-whitening efficiency is lowered: The reason can be inferred that the white inorganic particles contained in the sludge were caused to melt and sinter on papermaking due to the sharp thermal treatment of the sludge without the carbonization step. σ In the X-ray diffraction (picture) of the sample obtained in Comparative Example 2, there were no spikes of kaolin and calcium carbonate. The whiteness of the recovered sample was 74%. Due to the rapid heat treatment in the decarburization-whitening treatment, the melting and sintering of the white non-particles contained in the sludge occurred, resulting in a reduction in the whiteness improvement rate. In the x-ray diffraction (picture) of the sample obtained in Comparative Example 3, there were no peaks of high and calcium carbonate. The whiteness of the incineration ash is 54%, which is very low, which is for the papermaking raw materials. ^
527455 五、發明說明(31) (塗層紙之製造及白色度之測定) 其,,使此等試料充當造紙用之原米斗,以施行塗覆而予 以汗價。對各試料加水,而在固形物濃度6〇%為目 (A6028/東亞合成"公司商品名)以白色無機粒子基固 形分可成為0_ 5%之方式添加後’用分散機使之分散:製備 一漿體。又按,在全然未使用分散劑之場合, 機粒子之不均勻分散。將上述(藉分散劑分散之&漿體^使 用一砂磨機("ΑΙΜΕχ"公司)之下,予以濕式粉碎)至 徑達到2 · 0 # m為止。平均粒徑係用_ 句拉 測定妒置(5100/" · +. ” Sedlgraph粒度分布 、J疋衣置(5100/ micr〇meritlc公司)予以 又按,關於實施例2所得之試料, 60%之方式加水以製備一赞體之& j固形物浪度可達到 性。使此浆體在被二 :良好之分散裂體,即使在分散劑之率二是 此外’關於實施例2所得之試 濃度可達到15%之方式被加水之未人=衣備一種以固形物 體以PH13顯示鹼性。對此漿體灌3为散劑之聚體。此鳆 為11,使調整pH後之漿體脫水\ =氡化碳,以調整讪 6 0%。 δ周節固形物濃度為 此聚體亦由於藉二氧化竣所 分散劑之添加率(按固形公I & 甲和而改善流動性 於二氧化妷處理,降低了八μ · /g即得以充分分散。 刀政劑之添加率,造成經濟上: 一 11 - C:\2D-CODE\9(M 1\9〇117420·ptd 第36527455 V. Description of the invention (31) (manufactured coated paper and measurement of whiteness) The samples are made to serve as raw rice hoppers for papermaking, and they are coated with sweat. Water was added to each sample, and after the solid concentration was 60% (A6028 / East Asia " company name), the white inorganic particle-based solid content could be added to 0_5%, and then dispersed using a disperser: Prepare a slurry. Also, in the case where no dispersant is used at all, the organic particles are unevenly dispersed. The above-mentioned (dispersed & slurry ^ using a sand mill (" ΑΙΜΕχ ") and wet pulverized) until the diameter reached 2 · 0 # m. The average particle size is determined by _ Jula (5100 / " · +. ”Sedlgraph particle size distribution, J 疋 clothing set (5100 / micromerlc)), again, about the sample obtained in Example 2, 60% Water was added in a manner to make a solid body & j solids reachability. Make this slurry in the second layer: good dispersion cracking, even in the dispersant rate two is in addition to the 'obtained in Example 2 The test concentration can reach 15% in a way that has not been added to water = prepare a solid object with PH13 showing alkalinity. This slurry is filled with 3 as a polymer of powder. This is 11 to make the pH adjusted slurry Dehydration \ = tritium carbon to adjust 讪 60%. Δ weekly solids concentration for this polymer is also due to the addition rate of the dispersant by the completion of the dioxide (according to solid male I & a Thorium dioxide treatment reduced the amount of 8 μ · / g and was able to fully disperse. The addition rate of the knife agent caused economic:-11-C: \ 2D-CODE \ 9 (M 1 \ 9〇117420 · ptd 36th
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五、發明說明(32) 利之結果。 對所得到之各自含有試料之漿體添加澱粉("ace a" 子cornstarch”公司之商品名)2份,以及鹼增黏型王 丁二烯共聚物乳膠(JSR-0 6 9 3/" JSR,,公司之商。口 八烯〜 而得到塗料。 σ 7伤, 所得到之塗料以單面之乾燥固形分可成為i〇g/m2之 式藉台式桿塗機塗覆於48. 5g/m2之原紙之雙面上而得会冷 層紙。此項雙面塗層紙之白色度係在使用一分光白1到塗 色計("SUGA試驗機”公司製品)之下根據JIS p刀8 1 234測=測 者。各塗層紙之白色度乃示於表1中。 “义V. Description of Invention (32) Add 2 parts of starch (" ace a " trade name of "cornstarch") to each of the obtained slurry containing the sample, and alkali thickened type butadiene copolymer latex (JSR-0 6 9 3 / & quot JSR, the company's quotient. Octocene ~ to get coatings. Σ 7 wounds, the resulting coatings can be i〇g / m2 in the form of a single-sided dry solid content coated by a bench-top bar coater at 48. 5g / m2 of double-sided base paper can be obtained from cold-layer paper. The whiteness of this double-coated paper is based on the use of a spectro white 1 to a colorimeter (" SUGA testing machine "company product) according to JIS p knife 8 1 234 test = tester. The whiteness of each coated paper is shown in Table 1. "义
塗有實施例1〜4所得到之白色無機粒子之各紙試樣之白 色度為74%、82%、78%、82%,即為充分高之白色度,於是 確認均適於造紙用之原料。 、疋 塗有比較例1所得到之試料之紙之白色度為7 & %。雖然對 於泥在比實施例1為高80 0 溫度下施行熱處理,但所得到 之白色度卻與實施例1相等。為其脫碳—白化效率降低之原 因’如别所述,可推斷的是,由於不經過碳化步驟之於泥 之急劇熱處理,引起於泥所含之白色無機粒子發生在造紙 上不適合之熔融·燒結所致。The whiteness of each paper sample coated with the white inorganic particles obtained in Examples 1 to 4 was 74%, 82%, 78%, and 82%, which was a sufficiently high whiteness. Therefore, it was confirmed that all of the materials were suitable for papermaking. . The whiteness of the paper coated with the sample obtained in Comparative Example 1 was 7 &%. Although the mud was heat-treated at a temperature higher than that of Example 1, the obtained whiteness was equal to that of Example 1. The reason for its decarburization-decreased whitening efficiency 'As mentioned elsewhere, it can be inferred that the white inorganic particles contained in the mud caused unsuitable melting on papermaking due to the sharp heat treatment of the mud without going through the carbonization step. Caused by sintering.
對比較例2所得到之試料亦同樣一砂磨機(,,a丨ΜΕχ”公司) 予以濕式粉碎,但無法粉碎其燒結之粒子,於是無法用作 造紙用之原料。 塗有比較例3所得到之試料之紙之白色度為6 4 %,即為難 於用作塗層紙者。The sample obtained in Comparative Example 2 was wet-pulverized in the same way as a sand mill (a, MEX), but the sintered particles could not be crushed, so it could not be used as a raw material for papermaking. The whiteness of the obtained sample paper was 64%, which means that it is difficult to use as a coated paper.
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五、發明說明(33) (比較例4 ) 在比較例4中’為從於泥再生之白色無機粒子與市隹 面上所出售)顏料做比較。對市售顏料之重質碳酸鈣η市 (”1^(11*〇(:111^6-9 0丨丨/丨丨備北粉化丨丨公司之商品名)及2級古〜 土(HT/" ENGELHARD"公司之商品名)添加〇.5%之分散劑^嶺 量之pH調整劑(氫氧化鈉)以使分散於水中而製備—^及適 形分(固形物含量)60%之漿體。對此一顏料漿體添加職^固 ("ace AV1'王子cornstarch”公司之商品名)2份,以 增黏型苯乙烯-丁二烯共聚物乳膠㈠SR-〇 6 93厂,jSRn公司之V. Description of the invention (33) (Comparative Example 4) In Comparative Example 4, the comparison is made between white inorganic particles regenerated from mud and pigments sold on the market. For commercial pigments of heavy calcium carbonate η ("1 ^ (11 * 〇 (: 111 ^ 6-9 0 丨 丨 / 丨 丨 Beibei flour powder 丨 丨 Company name) and Grade 2 ancient ~ soil (HT / " ENGELHARD " company's trade name) is prepared by adding 0.5% of dispersant ^ ridge amount of pH adjuster (sodium hydroxide) to disperse in water-^ and conformable content (solid content) 60% Add 2 parts of this pigment paste (" ace AV1 'Prince Cornstarch "trade name) to thicken styrene-butadiene copolymer latex ㈠SR-〇6 93 Factory Of jSRn
商品名)7份,而得到塗料。與實施例一樣施行手塗而得到 塗層紙。對表1所示之實施例所得到之試料施予塗層之紙 之白色度,係與此寻市售顏料同等之白色度。 (實施例5 ) ^ 從與上述造紙工場 (造紙污泥)乃具有水 之經過熱風爐乾燥, 550 °C ,而在550 °C 〜 其次,以富氧狀送熱 處理1 2 0分鐘。於是 以此材料少量加入茶 如此處理所得到之 者,將此項材料加入 附色素等而使水溶液 證實該材料為具有多(Trade name) 7 parts to obtain a coating. Coated paper was obtained by performing hand coating in the same manner as in the examples. The whiteness of the coated paper obtained from the samples obtained in the examples shown in Table 1 is the same as the whiteness of this commercially available pigment. (Example 5) ^ From the above papermaking plant (paper sludge), it was dried in a hot air oven with water at 550 ° C, and then at 550 ° C ~ Second, it was heat-treated in an oxygen-rich state for 120 minutes. So add a small amount of this material to the tea. The result of this treatment is added to the material with pigments and so on to make the aqueous solution confirm that the material has more
不同之造紙步驟所排出之造紙淤泥 分(含水率)約6 5 %及視比重〇 . 8 5。使 其-人’藉貧氧加熱爐使之慢慢升溫」 6 0 0 C溫度下予以碳化處理3 〇分鐘。 風而在5 5 0 °c〜6 〇 〇 °C溫度下予以煅4 ’ $亍到一具有白色粒狀形狀之材料。 中’而予以攪拌時,茶色則變淡。 材料在外觀上呈白色系之顏色。再 有色混濁水或茶等之水溶液時,則$ 之顏色變淡,又吸附香煙之煙,因il 孔性之活性物質。The papermaking sludge (water content) discharged from different papermaking steps is about 65% and the apparent specific gravity is 0.85. Let it-human 'slowly raise the temperature by using an oxygen-depleted heating furnace. "Carbonization treatment was performed at a temperature of 600 ° C for 30 minutes. The material is calcined at a temperature of 5 50 ° C to 600 ° C to a material having a white granular shape. When it is stirred, the brown color becomes lighter. The material is white in appearance. When colored turbid water or an aqueous solution such as tea is used, the color of $ becomes lighter, and cigarette smoke is adsorbed because of the porous active substance of il.
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(貫施例6 ) (裝置之說明) 關於實施例6之炎罢搂、土 各丄 2 1為原料漏斗,22為机置I $ ^用圖4之下,加以說明。 戴切)裝置。23為用;又將所切原中料漏斗之下部之切料(原料 裝置,A為原料之乾燥;】切運送至乾燥裝置之 體,25為對乾燥楚置之熱^卞衣置A中’ 24為爐本 結之爐内運送裝置。30a、$ H衣置,26為以上下二段聯 定用之溫度計。B為Γ置:以Ϊ爐本體内部溫度之測 置。在碳化裝置B中,27 =衣置正中下方之碳化裝 爐内運送裝置,29為對蜂彳=盧壯本罢體,28為上下三段聯結之 _為碳化裝置爐本體^衣置供广之熱風之產生裝置。 用以將碳化之測定用之溫度計。Μ為 運送裝置。C、D為且有相^ $運送至煅燒裝置D之原料 置C中,32為原料篩選裝°構造之煅燒裝置。在煅燒裝 體内之水平多列式之炮^ ’、、,3為爐本體,34為設在爐本 裂置供給熱風之熱風產:;Π、:Λ5、36為用以對炮燒 螺桿機構34a,*隔該爐本體运\置34夕為由複數列之 續之材料保持板34b,以及螺^ έ 至之夕列圓筒形連 Μ、38為般燒裝置之上室及下\軸驅動裝/34c所構成。 溫度計。39為烺燒裝置所排出:::J :二:定用之 置。40為用以將冷卻裝置所排 I衣置及冷卻裴 置。42、43為锻燒裝置内之氧氣濃至貯槽之裝 44為煅燒裝置之廢氣之對運送 :用之运風裝置。 、V入用之導管,藉以(Exemplary Embodiment 6) (Explanation of the device) Regarding the flammability and soil of Example 6, 21 is the raw material funnel, 22 is the machine set I $ ^ will be described below with reference to FIG. 4. Daiche) device. 23 is used; cut the material in the lower part of the cut raw material funnel (raw material device, A is the drying of the raw material;) cut and transported to the body of the drying device, 25 is the heat placed on the dry place ^ 卞 clothing set in A ' 24 is the furnace conveying device in the furnace. 30a, $ H clothes set, 26 is the thermometer used in the above two steps. B is Γ: It is based on the internal temperature measurement of the oven body. In the carbonization device B , 27 = transport device in the carbonization furnace in the middle and lower part of the clothes set, 29 is the pair of bee stings = Lu Zhuangben, 28 is the upper and lower three links _ is the furnace body of the carbonization device ^ hot air generating device for the clothes set Thermometer for measuring carbonization. M is a conveying device. C and D are raw materials that are transported to the calcining device D in phase C. 32 is a calcining device with a screening structure of raw materials. In the calcining device Horizontal multi-row cannons in the body ^ ',,, 3 are the furnace body, 34 is a hot air product provided in the furnace to split hot air supply: Π,: Λ5, 36 are used to fire the screw mechanism 34a, * Operated by the furnace body, the night is set as a material holding plate 34b continued from a plurality of rows, and the cylindrical shape of the spiral row M, 38 It is composed of the upper chamber and the lower shaft drive device / 34c of the general burning device. The thermometer. 39 is discharged from the sintering device :: J: two: fixed use. 40 is used to line the cooling device. Place and cool Pei. 42 and 43 are the oxygen concentration in the calcining device to the storage tank. 44 is the pair of conveying waste gas of the calcining device: used for the wind transport device.
527455 五、發明說明(35) ---- &行運送裝置23内之々斗 1 生之p … 肩科之乾你者。45a為運送裝置所產 燥裝置Α所產生之水基★置47 \用之導管。45b為含有乾 導乾 ’、、、乳之廢乳之對脫臭裝置47導入用之 V官。46為導管,用以n ^六衣直V入用之 之廢#i + m入^^ 將攸運迗衣置23導入之原料乾燥用 理後妯φ夕鼓尸人风屬49近旁。48為經脫臭裝置脫臭處 氣抽弓丨風扇。50 Α麻" 水々夕管式冷卻裝置。49為廢 (原料之向大氣放出用之煙函。 泥ΐ:ΐ二中’Α用—屬於與上述實施例不同之造紙游 之脱墨游泥。其含水率為約50%,視比重凫n sR (原料之供給) 視比重為0.85。 ::存於原料漏斗内之脫墨於泥按一定量從 刀出去。將所切出之原料藉由運送 22 , 〇 ^ # 50kg/hr ^ ^ ^ ^ (原料之乾燥·碳化) 有 裳入乾燥裝置内之原料藉爐内運 水平方向予以移送。在乾燥|置八\本#體内沿 爐本體内供給之燃燒高溫氣體來施一之…、1產生衣置向 含之水分蒸發。在此期間,存在於^、S, ^加熱以使原料所 如空氣等乃被所產生之水蒸氣置換,运衣置内之含氧氣體 0 · 1 %以下之貧氧狀態。將上述乾於而形成一種氧氣濃度 裝入碳化裝置本體内。在碳化裝^ $理後之原料予以連續 29所供給之燃燒高溫氣體,將二邊在、’利=熱風產生裝置 一邊被乾燥之原料藉由運送裝置夕供,迗裝置内水平移動 之鐵皮予以間接加熱,而527455 V. Description of the invention (35) ---- & The bucket in the transporting device 23 1 The p of life ...... The shoulder shoulders you. 45a is a water-based tube produced by the drying device A produced by the transport device. Reference numeral 45b is a V-member for introducing a deodorizing device 47 containing waste milk, dry milk, and milk. 46 is a duct for n ^ Liu Yizhi V to use the waste #i + m 入 ^^ After drying the raw materials introduced by Youyun clothing set 23, 妯 xi drum corpse wind is near 49. 48 is a deodorizing place through a deodorizing device. 50 Α 麻 " Water tube cooling device. 49 is a waste (a letter for the release of raw materials to the atmosphere. Loach: ΐ 二 中 'Α 用 —It is a deinking sludge that is different from the above-mentioned papermaking sludge. Its moisture content is about 50%, depending on the specific gravity.) n sR (supply of raw materials) The apparent specific gravity is 0.85. :: The deinked mud stored in the raw material funnel is removed from the knife by a certain amount. The raw materials cut out are transported by 22, 〇 ^ # 50kg / hr ^ ^ ^ ^ (Drying and carbonization of raw materials) The raw materials that have been put into the drying device are transported horizontally by the furnace. In the drying | Set eight \ 本 # body, the burning high-temperature gas supplied along the body of the furnace to apply one ... 1 and 1 produce evaporation of the moisture contained in the clothes. During this period, the existence of ^, S, ^ is heated so that the raw materials such as air are replaced by the generated water vapor, and the oxygen-containing gas in the clothes is transported 0 · 1 Oxygen-depleted state below%. The above-mentioned drying process forms an oxygen concentration into the body of the carbonization device. The raw material after carbonization is treated with continuous high-temperature gas supplied by 29, and the two sides are at The raw materials that are dried on one side of the hot air generating device are supplied by the conveying device, and the inside of the device moves horizontally. Moving iron sheet indirectly heats, and
C:\2D-CODE\90-ll\90117420.ptd 第40頁 527455 五、發明說明(36) 使其爐内氣氛溫度達到60 0。(:。在此期間,含氧氣體如空 氣等乃被碳化裝置所產生之乾餾氣體完全置換,而形成一 種氧氣濃度低於0· 1%之貧氧狀態下之還原氣氛,於是促進 有機物之碳化。在本實施例巾,為脫墨造紙淤泥之連續處 理,將淤泥在碳化裝置爐内之滯留時間設定為3〇分鐘。在 所產生之碳化物中,有機物由來之固定石炭所佔之比率平均 值為W重量比)。碳化裝置所排出之原料(碳化物)之排出 量由於施行乾燥·碳化處理而成為49kg/hr。 (碳化物之白化處理) 將碳化室B所排出之碳化物藉由運送裝置 入锻燒,置C,。所導入之燃燒氣體之氧氣濃度有可能依照 燃燒空虱比亚利用达風1機(風扇)之空氣附加手段予以調整 至3%至15%,而在本實施例係將炮燒裝置c之爐内氧氣濃戶 ,定為12%。般燒裝置C之爐内溫度係有可: 貫施例將此項溫度設定為65(rc。藉運送裝置之螺旋機構本 施打般燒對象物在該氣氛+之水平移動及料,而 行利用氧氣之脫碳反應。將碳化物在煅燒裝置“盧内之二 留時間設定為80分鐘。將煅燒裝置c所排出之 連續裝入設置於該裝置下部之炮燒裝置D ; 度乃與上部之緞燒裝置C —樣予以設定為】 D之爐内溫度設定為75Gt。將炮燒對象物在炮=置 内之滯留時間設定為40分鐘。炮燒裝置㈣ ^衣置^盧 排出量由於施行煅燒處理而成為4〇kg/hr。 原料之 (處理結果) 527455C: \ 2D-CODE \ 90-ll \ 90117420.ptd Page 40 527455 V. Description of the invention (36) Make the temperature of the atmosphere in the furnace reach 60 ° C. (:. During this period, oxygen-containing gas such as air is completely replaced by the carbonized gas produced by the carbonization device, and a reducing atmosphere in an oxygen-depleted state with an oxygen concentration lower than 0.1% is formed, thereby promoting the carbonization of organic matter. In this example, for the continuous treatment of deinking papermaking sludge, the residence time of the sludge in the carbonization device furnace was set to 30 minutes. Among the carbides produced, the ratio of fixed carbon derived from organic matter was averaged. The value is W weight ratio). The discharge amount of the raw materials (carbides) discharged from the carbonization device is 49 kg / hr due to the drying and carbonization treatment. (Carbide whitening treatment) The carbide discharged from the carbonization chamber B is put into a calcination by a conveying device, and C is placed. The oxygen concentration of the imported combustion gas may be adjusted to 3% to 15% according to the air addition method of the Dafeng 1 machine (fan). In this embodiment, the furnace of the firing device c is used. The concentration of oxygen in households is set at 12%. The temperature in the furnace of the general firing device C is available: The temperature is set to 65 (rc) in the embodiment. The spiral mechanism of the conveying device is used to move the general object at the level of the atmosphere +. The decarburization reaction using oxygen. The retention time of the carbides in the calcining device "Lunei" is set to 80 minutes. The discharge from the calcining device c is continuously charged into the firing device D provided at the lower portion of the device; The satin-burning device C is set as follows] The temperature in the furnace of D is set to 75 Gt. The residence time of the object to be burned in the gun is set to 40 minutes. The firing device ㈣ ^ clothing set ^ discharge volume due to The calcination treatment is performed to obtain 40 kg / hr. Of the raw materials (treatment result) 527455
::、士述條件使用本設備以施行操作之結果,得 色度85%之碳酸鈣為主成分之無機物。 弓經過評價後得到之結果為,處理前之^化 侧口熱處理而分解成氧化妈之比率為衛广。物所…以 二所:收之白色無機物與水混合而成之水(混)濁液之pH : 安白色無機物:水=6 〇 : 4 0之混合狀態(漿體化)之太::, According to the conditions described, the operation of this equipment was used to obtain an inorganic substance with calcium carbonate as the main component of 85% color. After the bow was evaluated, the result was that the ratio of the heat treatment at the side of the mouth before the treatment to the decomposition into the oxide mother was Wei Guang. Objects: No.2: pH of water (mixed) turbid liquid obtained by mixing white inorganic matter with water: An white inorganic matter: water = 6 〇: 40 in a mixed state (slurry)
:液在黏度上發生惡化者屬微量。因&,在造紙步驟中使 :白色無機物漿體化而予以運送之際,不需要施行現有生 J設:之改造。再者,已確認、,在使用此項白色無機 以、我y驟上之表面塗覆材料時,可用作現在所用之碳酸鈣 之代替材料。將本處理結果予以綜合展示於 表2 項目 乾燥裝置 碳化裝置 烺燒裝置 (上段) 烺燒裝置~— (下段) 爐内溫度 450〇C __600°C 650〇C ---V J__ 750〇C ' 爐内滯留時間 20分鐘 ___分鐘 8分鐘 40分鐘 氧氣濃度 一 低於0. 1 裝置容器) 12% (爐内) 12% — (爐内) 處理後之成分 之性狀 含水率:0. 1% 固定碳:平均8% 無機物:平均90% 一 \ J 白色度 :平 CaC〇3分解率:平均4〇% 水濁液之pH : 12 [發明之效果]: Traces of liquid deterioration in viscosity. When & the white inorganic slurry is transported in the papermaking step and transported, there is no need to carry out the transformation of existing facilities. In addition, it has been confirmed that the white inorganic surface coating material can be used as a substitute material for calcium carbonate currently used. The results of this treatment are comprehensively shown in Table 2. Carbonization device of the project drying device Burning device (upper section) Burning device ~ — (lower section) Furnace temperature 450 ° C __600 ° C 650 ° C --- V J__ 750 ° C ' The residence time in the furnace is 20 minutes ___ minutes 8 minutes 40 minutes. The oxygen concentration is less than 0.1. 1 Device container) 12% (in the furnace) 12% — (in the furnace) Properties of the components after treatment Moisture content: 0.1 % Fixed carbon: Average 8% Inorganic matter: Average 90% I \ J Whiteness: Plain CaC03 Decomposition rate: Average 40% pH of water turbid liquid: 12 [Effect of the invention]
五、發明說明(38) — 物之碳化及脫碳-白化。即,勺 含有屬於廢棄物之有機物/下述二步驟為其特徵:對 含氧氣體之存在之貧氧狀況二機粒子之混合物在限制 (以450 °c〜70 0 °C之範圍較户)A,1 0 0 0 C以下之溫度範圍 將該石炭化處理所得到之碳化土=加碳化處理之步驟;其次 °c〜1〇〇(TC溫度範圍内氧化之可令該碳,物在45〇 下予以脫碳而達成白色無機粒子:乳乱體之存在 8〇〇/ " L 土以、、 他祖于之白色度為70%以上(以 “上較幻之脫碳-白化處理步騍。依照本方法,可回 收:具有優異之磨耗性及安定之品f之白色無機粒子。 =外’在碳化處理中’例如在40 0。〇以下之溫度下施行 ^刀蒸發 ’ m4〇(rc〜100(rc<qnwttM, =此經過二階段以上之加熱帶時,可實現安定之碳化處 理〇 在脫碳-白化處理中,以700 t〜800為較佳之溫度範 圍,經過45(TC〜6 0 0 Ό與60〇它〜1〇〇〇1之二階段或更多 階,之加熱帶時,可藉此實現更安定之處理而得到進一步 提鬲白色度之效果。 。依照含氧氣體之供給量將脫碳-白化處理溫度調節為8 〇 〇 C以下時,可藉此回收具有更優異之磨耗性之白色無機粒 子。 此外,在處理前之廢棄物中含有高嶺石之場合,使高嶺 石非晶質化而使锻燒高屬土變性時,可藉此提高白色度。 再者,本發明之回收白色無機粒子之方法為,在碳化處 理後使碳化物冷卻時,有可能藉此施行更充分之脫碳,另V. Description of the invention (38) — Carbonization and decarbonization of white matter. That is, the spoon contains organic matter that belongs to waste / The following two steps are characteristic: the mixture of two organic particles is limited to the oxygen-depleted condition of the presence of oxygen-containing gas (the range is 450 ° c ~ 70 0 ° C compared with households) A, 1 0 0 0 C or lower temperature range, the carbonized soil obtained from the carbonization treatment = the step of carbonization treatment; second ° c ~ 100 (the oxidation in the TC temperature range can make the carbon, 45 Decarbonization below 〇 to achieve white inorganic particles: the existence of turbulent body 8000 / "L Tu Yi, and his ancestors have a whiteness of more than 70% (the" more magical decarburization-whitening treatment step "骒. According to this method, white inorganic particles with excellent abrasion resistance and stable product f can be recovered. = Outer 'in the carbonization process', for example, ^ knife evaporation' is performed at a temperature of 40 0. rc ~ 100 (rc < qnwttM, = stable carbonization can be achieved when the heating belt is passed through two or more stages. In decarburization and whitening treatment, 700 t ~ 800 is the preferred temperature range. After 45 (TC ~ 6 0 0 Ό and 60 〇 it ~ 10000 two or more stages, when heating the zone, This achieves a more stable treatment and further improves the whiteness. When the temperature of the decarburization-whitening treatment is adjusted to below 800 ° C according to the supply amount of oxygen-containing gas, it can be recycled to have more excellent abrasion In addition, when the kaolinite is contained in the waste before the treatment, the kaolinite can be made amorphous and the calcined kaolin soil can be modified to improve the whiteness. Furthermore, the present invention can improve the whiteness. The method of recovering the white inorganic particles is that when the carbide is cooled after the carbonization treatment, it is possible to perform a more sufficient decarburization by this, and
C:\2D-O0DE\9CMl\90117420.ptd 第43頁 527455 五、發明說明(39) 在 增 加 碳 化 物 之 比 表 面 積 時 , 有可 能藉此 在更 佳之條 件下 以 良 好 之 效 率 施 行 後 段 之 脫 石炭 -白化處理者。 此 外 5 將 由 白 色 無 機 粒 子 經 水性 媒體稀 釋所 得之水 性懸 浮 液 最 好 能 在 使 用 二 氧 化 碳 之 下調 整其pH 為8〜1 3時^ 丨可 藉 此 安 定 使 用 所 回 收 之 白 色 無 機粒 子。又 可有 效調整 白色 無 機 粒 子 之 粒 徑 Ο 此 外 , 在 使 用 本 發 明 有 關 之 方法 來處理 造紙 淤泥時 ,有 機 成 分 則 被 碳 化 而 無 機 成 分 之構 造則維 持原 狀,因 此有 可 能 重 複 利 用 於 造 紙 步 驟 上 ? 亦有 可能被 運用 於可利 用多 孔 性 之 性 質 之 領 域 〇 [元件編號之說明] 1 第 一 間 接 加 熱 爐 (碳化步驟之乾燥帶) 2 於 泥 投 入 D 3 淤 泥 乾 燥 室 4a 熱 風 進 入 Π 4b 熱 風 進 入 Π 4c 熱 風 進 入 Π 5a 熱 風 水 蒸 氣 以 及 乾餾 氣體之 排出 π 5b 熱 風 水 蒸 氣 、 以 及 乾餾 氣體之 排出 V 5c 熱 風 排 出 D 6 第 二 間 接 加 熱 爐 (碳化步驟之藉熱分解之碳化帶) 7 淤 泥 之 熱 分 解 及 碳 化 室 8 碳 化 物 排 出 Π 9 碳 化 物 移 送 流 路 ill sC: \ 2D-O0DE \ 9CMl \ 90117420.ptd Page 43 527455 V. Description of the invention (39) When increasing the specific surface area of the carbide, it is possible to use this method to perform the decarbonization of the later stage under better conditions and with good efficiency. -Albino processor. In addition, the aqueous suspension liquid obtained by diluting the white organic particles with an aqueous medium is best to adjust its pH to 8 ~ 13 when using carbon dioxide ^. This can be used to stabilize and use the recovered white organic particles. It can also effectively adjust the particle size of the white inorganic particles. In addition, when using the method of the present invention to treat papermaking sludge, the organic component is carbonized and the structure of the inorganic component is maintained intact, so it is possible to reuse it in the papermaking step? It may also be used in areas where the properties of porosity are available. [Explanation of the element number] 1 The first indirect heating furnace (drying zone of the carbonization step) 2 Put in the mud D 3 Sludge drying chamber 4a Hot air enters Π 4b Hot air enters Π 4c Hot air entering Π 5a Hot air steam and dry distillation gas π 5b Hot air steam and dry distillation gas V 5c Hot air discharge D 6 Second indirect heating furnace (carbonization zone by heat decomposition of carbonization step) 7 Sludge Thermal decomposition and carbonization chamber 8 Carbide discharge Π 9 Carbide transfer flow path ill s
m 11 11· C:\2D-CODE\90-ll\90117420.ptd 第44頁 527455 五、發明說明 (40) 10 第三間接加熱爐(脫碳-白化帶) 11 碳化物投入口 12 空氣進入口 13 脫碳-白化室 14 白色無機粒子回收 α 15 内燃式旋窯(脫碳- 白化帶) 16 碳化物儲存器 17 碳化物投入口 18 碳化物氧化室 19 燃燒器 20 白色無機粒子回收 口 21 原料漏斗 22 切料裝置 23 運送裝置 24 爐本體 25 熱風供給裝置 26 爐内運送裝置 27 爐本體 28 爐内運送裝置 29 熱風產生裝置 30b 溫度計 31 原料運送裝置 32 原料篩選裝置 33 爐本體 «m 11 11 · C: \ 2D-CODE \ 90-ll \ 90117420.ptd Page 44 527455 V. Description of the invention (40) 10 Third indirect heating furnace (decarbonization-whitening belt) 11 Carbide inlet 12 Air entering Port 13 Decarburization-whitening chamber 14 White inorganic particle recovery α 15 Internal combustion rotary kiln (decarbonization-whitening belt) 16 Carbide reservoir 17 Carbide input port 18 Carbide oxidation chamber 19 Burner 20 White inorganic particle recovery port 21 Raw material hopper 22 Cutting device 23 Conveying device 24 Furnace body 25 Hot air supply device 26 Furnace conveying device 27 Furnace body 28 Furnace conveying device 29 Hot air generating device 30b Thermometer 31 Raw material conveying device 32 Raw material screening device 33 Furnace body «
C:\2D-CODE\90-ll\90117420.ptd 第45頁 527455C: \ 2D-CODE \ 90-ll \ 90117420.ptd Page 45 527455
五、> 發明說明 (41) 34 烺 燒 物 運 送 裝 置 35 '36 献 風 產 生 裝 置 37 、38 溫 度 計 39 原 料 運 送 裝 置 及冷卻裝置 40 原 料 運 % \/ 达 裝 置 41 貯 槽 42 、43 送 風 裝 置 44 導 管 45 a 、 45b 導 管 46 導 管 4 7 脫 臭 裝 置 48 水 冷 多 管 式 冷 卻裝置 49 抽 氣 風 扇(廢棄抽引風扇) 50 煙 囪 C:\2D-CODE\90-ll\90117420.ptd 第 46 頁 527455 圖式簡單說明 圖1為本發明之回收白色無機粒子之方法之程序圖。 圖2為用以施行本發明之碳化步驟及脫碳-白化處理步驟 之熱處理裝置一例之概略系統圖。 圖3為用以施行本發明之碳化步驟及脫碳-白化處理步驟 之熱處理裝置另一例之概略系統圖。 圖4展示一應用於本發明實施例6之裝置之例子。Fifth, > Description of the invention (41) 34 Burning material conveying device 35 '36 Air supply generating device 37, 38 Thermometer 39 Raw material conveying device and cooling device 40 Raw material conveying% \ / reaching device 41 storage tank 42, 43 air supply device 44 duct 45 a, 45b Conduit 46 Conduit 4 7 Deodorizing device 48 Water-cooled multi-tube cooling device 49 Extraction fan (abandoned extraction fan) 50 Chimney C: \ 2D-CODE \ 90-ll \ 90117420.ptd Page 46 527455 Figure 46 Brief Description of Formulas FIG. 1 is a flowchart of a method for recovering white inorganic particles according to the present invention. Fig. 2 is a schematic system diagram of an example of a heat treatment apparatus for performing the carbonization step and the decarburization-whitening treatment step of the present invention. Fig. 3 is a schematic system diagram of another example of a heat treatment apparatus for performing the carbonization step and the decarburization-whitening treatment step of the present invention. FIG. 4 shows an example of an apparatus applied to Embodiment 6 of the present invention.
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