TWI305787B - Device and process for plastic pyrolysis - Google Patents

Device and process for plastic pyrolysis Download PDF

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TWI305787B
TWI305787B TW94147655A TW94147655A TWI305787B TW I305787 B TWI305787 B TW I305787B TW 94147655 A TW94147655 A TW 94147655A TW 94147655 A TW94147655 A TW 94147655A TW I305787 B TWI305787 B TW I305787B
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Taiwan
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cracking
plastic
oil
halogen
hydrocarbon
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TW94147655A
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Chinese (zh)
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TW200724575A (en
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Shun Chih King
Chiung Fang Liu
Chih Hao Chen
Jia Ming Huang
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Ind Tech Res Inst
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

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  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Processing Of Solid Wastes (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Description

;305787 九、發明說明: 【發明所屬之技術領域】 本發明是有關於一種裂解塑膠的方法以及塑膠裂解裝 置’特別是有關於一種可提升油品液化率、降低油品中氯含^ 之裂解塑膠的方法以及塑膠裂解裝置。 【先前技#f】 我國廢棄塑膠的年產量約為一百萬公嘲,佔家庭廢棄物的 φ 16% ’比起歐(8%)、美(7%)國家,明顯偏高。廢塑膠由各種不 同塑膠混合而成,常見的包括:聚氯乙烯(p〇lyvinyl chbride, PVC)、聚乙烯(polyethylene,PE)、聚丙烯(p〇lypr〇pyiene, pp)、 聚苯乙烯(polystyrene, PS)、丙烯腈-丁二烯-苯乙烯共聚體 (Acrylonitrile Butadiene Styrene, ABS)、紛搭樹脂(Phenolic)、尿 素樹脂(Urea)、三聚氰胺樹脂(Melamine)、環氧樹脂(Ep0Xy)、 不飽和聚酯(Unsaturated Polyester)以及聚氨基甲酸酉旨 (Polyurethane)等。我國的廢塑膠處理工廠,每年可處理廢塑膠 鲁量约七萬11 镇,佔廢塑膠總量的7%左右,而處理的塑膠種類則 集中於熱塑性塑膠,例如PVC、PP、PE、PS或ABS等。早期 廢塑膠的降解研究一般均以PE、PS、PP為對象,較少探討pvc 的降解機制。 過去二十年間,廢塑膠增加的速率遠超過塑膠生產的速 率。如此大量的塑膠廢棄物,若以焚化方式處理,將會造成環 境污染及資源的浪費。 在眾多含鹵素成份的塑膠中,聚氯乙烯(polyvinyl 〇718-A21362TWF(N2);P1〇94〇〇35TW;shine 5 ϋ〇5787 chloride PVC)由於其成本低、加工性佳、耐熱、耐燃、電絕 緣性優' =及良料耐化學腐錄,因此廣泛地使用於各種工 業中,、產量與使用量極大,也因此產生大量的pvc廢棄物, 而造成相當困擾的環保課題。 傳統上,是利用熱裂解技術處理廢棄塑膠,將有機廢棄物 轉=液態燃油而回收再利用,來避免廢棄物直接排放或丟棄 於環境中而造成污染。所謂的熱裂解,是指在適當的溫度以及 缺氧狀態下進行熱分解,此時聚合物的結構會斷裂成較小的中 •、間產物’這些中間產物可被用來作為石油化學工業的燃料或原 料使用、,而達到資源回收再利用的目的。熱裂解可以處理許多 種類的歸,並摻雜混合如木材、紙類或油漆等其他物質,且 不曰每成氣體體積增加,亦不會產生戴奥辛伽X排放的問 題。 然而,由於廢塑膠中摻雜著許多含鹵素成份的塑膠,這類 廢娜於裂解過程中會產生具有毒害性及腐純的齒化氮,造 成裂解爐及相關設備的腐钱,並且會影響液態燃油的品質及其 響應用,成為處理廢棄轉物過程巾最大的困擾。 第1圖㈣的是傳統的塑縣解裝置⑽,包括裂解槽 ιοί、進料供應槽in、氮氣供應槽113、冷凝器⑽、閥⑵、 闕I23以及管線m。將廢棄塑膠置於進料供應槽⑴,以批 次(Batch)方式供應至裂解槽1〇1,配合來自氮氣供應槽113所 供應的氮氣,裂解該裂解槽1Q1巾_棄歸,經過降解 (degrade)後所得到的有機氣體藉由管線ιΐ6⑽送至冷凝器 105中冷凝,無法冷凝的氣體經由闕123排出,冷凝液則經由 0718-A21362TWF(N2); P10940035TW;shine 6 1305787 閥121排出收集,而得到液態油品。 上述液態油品可作_油㈣。然而, 則廢棄塑膠中含有PVC,則在裂解過程中,會產 害性t餘性的氯化氫,造成裂解爐及其他的雜,並影 響液態油品的品質而限制其應用。 為了降低油品中的氯含量,各界無不致力於研究改善此議 題。305787 IX. INSTRUCTIONS: [Technical field of invention] The present invention relates to a method for cracking plastic and a plastic cracking device, particularly relating to a method for improving oil liquefaction rate and reducing chlorine content in oil products. Plastic method and plastic cracking device. [Previous technology #f] The annual output of discarded plastics in China is about one million taunts, and the φ 16% of household waste is significantly higher than that of Europe (8%) and the United States (7%). Waste plastics are made of a variety of different plastics, including: polyvinyl chloride (p〇lyvinyl chbride, PVC), polyethylene (polyethylene, PE), polypropylene (p〇lypr〇pyiene, pp), polystyrene ( Polystyrene, PS), Acrylonitrile Butadiene Styrene (ABS), Phenolic, Urea, Melamine, Ep0Xy, Unsaturated Polyester and Polyurethane. China's waste plastics processing plant can handle about 710,000 towns of waste plastics per year, accounting for about 7% of total waste plastics, while the types of plastics processed are concentrated in thermoplastics such as PVC, PP, PE, PS or ABS, etc. Early degradation of waste plastics is generally based on PE, PS, and PP, and less on the degradation mechanism of pvc. Over the past two decades, the rate of increase in waste plastics has far exceeded the rate of plastic production. Such a large amount of plastic waste, if disposed of by incineration, will cause environmental pollution and waste of resources. Among the many halogen-containing plastics, polyvinyl chloride (polyvinyl 〇718-A21362TWF(N2); P1〇94〇〇35TW; shine 5 ϋ〇5787 chloride PVC) has low cost, good processability, heat resistance and flame resistance. Excellent electrical insulation' = and good chemical resistance, so it is widely used in various industries, and the output and usage are extremely large, so a large amount of pvc waste is generated, which causes quite troublesome environmental protection problems. Traditionally, thermal cracking technology has been used to treat waste plastics, and organic wastes have been converted to liquid fuels for recycling, so as to avoid direct discharge of waste or disposal in the environment. The so-called thermal cracking refers to thermal decomposition at an appropriate temperature and under anoxic conditions, in which the structure of the polymer breaks into smaller intermediates and intermediate products. These intermediates can be used as petrochemical industry. Use fuel or raw materials for recycling purposes. Thermal cracking can handle many types of homing and dope with other materials such as wood, paper or paint, and does not increase the volume of each gas, nor does it cause Dioxin X emissions. However, because the waste plastic is doped with many plastics containing halogen components, such wastes will produce poisonous and rot-toothed tooth nitrogen during the cracking process, causing the corruption of the cracking furnace and related equipment, and will affect The quality of liquid fuel and its response have become the biggest problem in dealing with waste transfer process towels. Figure 1 (d) is a conventional plastic disintegration device (10) comprising a cracking tank ιοί, a feed supply tank in, a nitrogen supply tank 113, a condenser (10), a valve (2), a crucible I23, and a line m. The waste plastic is placed in the feed supply tank (1), and is supplied to the cracking tank 1〇1 in a batch manner, and the nitrogen gas supplied from the nitrogen supply tank 113 is mixed, and the cracking tank 1Q1 is discarded and discarded. The organic gas obtained after degrade) is sent to the condenser 105 for condensation by the line ι 6 (10), and the uncondensable gas is discharged through the crucible 123, and the condensate is discharged through the 0718-A21362TWF (N2); P10940035TW; the shine 6 1305787 valve 121. And get liquid oil. The above liquid oil can be used as _ oil (four). However, if PVC is contained in the waste plastic, hydrogen chloride will be produced during the cracking process, causing cracking furnaces and other impurities, which will affect the quality of the liquid oil and limit its application. In order to reduce the chlorine content in the oil, all parties are committed to research to improve this issue.

⑨^漏1187專利提出—種廢歸之脫氯程序,其裝置為循 環式流體化爐床,藉由將廢塑膠加熱至25〇〜35〇。〇,將塑膠中 之含氯成分以HC1的形式釋出,再以驗性液體加以吸收之,以 達成脫氣之目的。 US6346220專利藉著脫氯爐内之轉動刀片,提供廢塑膠在 脫氯爐内之移動並供應其熱量,以進行熱分解作用。 US4031192專利藉由將廢pvc塑膠或含氯廢塑膠在密閉 容器中以過熱蒸汽的方式將HC1分離出來。 JP2〇00191826專利提供-種廢塑膠熱裂解回收氣體及油 品裝置,裂解後之氣體自桶槽之頂端收集,萃取後之油品則由 底部收集,裂解的溫度控制在350〜45(TC,油品中的含氯成分, 則利用氧化鐵為觸媒加以吸收去除。 JP06065585專利之重點在於將含氯廢塑膠及觸媒混合, 並以螺旋進料器方式進料,而觸媒則以氧化鎳、氧化鋇、氧化 鋅、氧化鉻為主。 JP07192499專利藉由在廢塑膠裂解過程中加入觸媒(錦 化合物)’並將溫度控制在150〜400°C,而油品中之氯成分會 0718-A21362TWF(N2);P 10940035TW;shine 7 1305787 以HC1的形式被觸媒所吸附。 CN2649590專利將含氯廢塑料與200〜40(TC的熱介質(其 為水蒸氣或水蒸氣與其他非氧化性氣體的混合氣體)在反應器 中直接加熱,裂解後所得到的HC1溶液和脫氯後的廢塑料可回 收再利用。 TW294686專利提出一種塑膠廢棄物之熱裂解方法,在熱 裂解容器内熱裂解一熔融塑膠,將形成的氣狀產物送入一分顧 才主’使南沸點產物、有害氣體、不凝烴氣和低彿點產物分離, 將該有害氣體,不凝烴氣和低沸點產物送入一含_素鍛燒爐, 當再加熱該高沸點產物時,部分該再加熱高沸點產物循環至上 述熱裂解容器’將殘餘部分送至沸石觸媒層作催化轉化,由該 熱裂解容器下方取出於熱裂解步驟中塑膠廢棄物熱裂解形成 之殘餘物。 - TW445273專利藉由在一驟冷氣化器之反應區内將塑膠 裂解油予以部分氧化,其中該裂解油係在一非催化部分氧化反 應中作為主要烴反應物以生成一含有卣化氫的合成氣體,驟冷 該合成氣體,其係在該氣化器之驟冷區内將該合成氣體予以驟 冷,其中該合成氣體係與含有充足中和劑之驟冷水相接觸,以 凝結且t和該合成氣體中之齒化氫,並藉此形成自該驟冷水分 離出且回收之凝結鹵化鹽及實質免除齒素之合成氣體。 然而,上述專利的裝置或步驟較為複雜,且油品的液化率 及鹵素成份的去除效果有限。 【發明内容】 0718-A21362TWF(N2);Pl0940035TW;shine 8 之一在於提供—種裂解塑膠 用觸媒與吸收劑,用以降低 品質,減少氯成分對環境及The 9^ leak 1187 patent proposes a waste dechlorination process, which is a circulating fluidized hearth by heating the waste plastic to 25 〇 35 〇. 〇, the chlorine component of the plastic is released in the form of HC1, and then absorbed by the test liquid to achieve the purpose of degassing. The US6346220 patent provides the movement of waste plastics in a dechlorination furnace and supplies its heat by means of a rotating blade in a dechlorination furnace for thermal decomposition. The US4031192 patent separates HC1 by superheated steam in a closed container by using waste pvc plastic or chlorine-containing waste plastic. JP2〇00191826 patent provides a waste plastic thermal cracking recovery gas and oil device. The cracked gas is collected from the top of the tank. The extracted oil is collected from the bottom, and the cracking temperature is controlled at 350~45 (TC, The chlorine-containing component in the oil is absorbed and removed by using iron oxide as a catalyst. The JP06065585 patent focuses on mixing chlorine-containing waste plastics and catalysts and feeding them in a screw feeder, while the catalyst is oxidized. Nickel, cerium oxide, zinc oxide, chromium oxide. JP07192499 patent by adding catalyst (complex compound) in the cracking process of waste plastics and controlling the temperature at 150~400 °C, and the chlorine component in the oil will 0718-A21362TWF(N2);P 10940035TW;shine 7 1305787 is adsorbed by the catalyst in the form of HC1. The CN2649590 patent uses chlorine-containing waste plastics with 200~40 (TC heat medium (which is water vapor or water vapor and other non- The mixed gas of oxidizing gas is directly heated in the reactor, and the obtained HC1 solution and the dechlorinated waste plastic can be recycled and reused. The TW294686 patent proposes a thermal cracking method for plastic waste. Thermally cracking a molten plastic in a cracking vessel, and sending the formed gaseous product into a branch to separate the south boiling point product, harmful gas, non-condensable hydrocarbon gas and low-folk point product, and the harmful gas, non-condensable hydrocarbon The gas and the low boiling point product are fed to a kiln-containing calciner. When the high-boiling product is reheated, part of the reheated high-boiling product is recycled to the above-mentioned thermal cracking vessel', and the residual portion is sent to the zeolite catalyst layer for catalytic conversion. The residue formed by thermal cracking of the plastic waste in the thermal cracking step is taken from below the thermal cracking vessel. - TW445273 patent partially oxidizes the plastic cracking oil by reacting in a reaction zone of a quenching gasifier, wherein the cracking oil Is used as a main hydrocarbon reactant in a non-catalytic partial oxidation reaction to form a synthesis gas containing hydrogen halide, and quenching the synthesis gas, which is quenched in the quenching zone of the gasifier Wherein the syngas system is contacted with quench water containing sufficient neutralizing agent to coagulate and t and the hydrogenated hydrogen in the synthesis gas, thereby forming a separation and recovery from the quench water The condensed halogenated salt and the synthetic gas which is substantially free of dentate. However, the device or the step of the above patent is complicated, and the liquefaction rate of the oil and the removal effect of the halogen component are limited. [Summary of the Invention] 0718-A21362TWF(N2); Pl0940035TW; One of shine 8 is to provide a catalyst and absorbent for cracking plastics to reduce the quality and reduce the chlorine content to the environment.

1305787 有鑑於此,本發明的目的 的方法’藉由在裂解過程中使 油品中的氯含量,以提升油品 生態的危害。 本發明的另—目的,在於提供一種裂解塑膠的方法 由在裂解過程巾使㈣媒與吸收劑,用以降低油品中的平 均碳數、碳數分布以及減少裂解時間,以提升油品品 並減少能源消耗。 本發月的又目的,在於提供一種裂解塑膠的方法,藉 由兩階段方式裂解廢棄塑膠,在熱裂解過程中配合觸媒與 吸收剤的使用,用以提升油品之液化率並降低油品中的氯 含量,使油品之品質優良,更適合用於燃料或化學原料。 根據上述目的,本發明提供一種塑膠裂解裝置,包括第 一裂解槽、第二裂解槽以及冷凝器,第一裂解槽是用以將含鹵 素塑膠嫁融裂解而形成混合物,其包括鹵化氫與齒代烴,第二 裂解槽連接於第一裂解槽,用來容納Fe〇(〇H)及CaC03,其 中,Fe〇(〇H)作為觸媒,用以分解鹵代烴而形成無鹵素烴類以 及鹵素成分’ CaC03作為第一吸收劑,用以吸收鹵化氫以及鹵 素成分,冷凝器連接於第二裂解槽。 本發明提供一種裂解塑膠的方法,包括:(a)提供含鹵 素塑膠,(b)在300-550QC之間裂解含鹵素塑膠而形成混合 物,其包括鹵化氫與鹵代烴,(c)在330-420GC之間藉由1305787 In view of this, the method of the present invention enhances the ecological ecology of the oil by increasing the chlorine content of the oil during the cracking process. Another object of the present invention is to provide a method for cracking plastics by using (four) medium and absorbent in the cracking process to reduce the average carbon number, carbon number distribution and cracking time in the oil to enhance the oil product. And reduce energy consumption. The purpose of this month is to provide a method for cracking plastic, which is used to crack the waste plastic in a two-stage manner, and the use of the catalyst and the absorption enthalpy in the thermal cracking process to enhance the liquefaction rate of the oil and reduce the oil. The chlorine content in the oil makes the oil quality good and is more suitable for fuel or chemical raw materials. According to the above object, the present invention provides a plastic cracking device comprising a first cracking tank, a second cracking tank and a condenser. The first cracking tank is used for marrying and melting a halogen-containing plastic to form a mixture comprising hydrogen halide and teeth. Hydrocarbon generation, the second cracking tank is connected to the first cracking tank for accommodating Fe〇(〇H) and CaC03, wherein Fe〇(〇H) is used as a catalyst to decompose halogenated hydrocarbons to form halogen-free hydrocarbons. And a halogen component 'CaC03 as a first absorbent for absorbing hydrogen halide and a halogen component, and the condenser is connected to the second cracking tank. The present invention provides a method of cracking a plastic comprising: (a) providing a halogen-containing plastic, (b) cracking a halogen-containing plastic between 300-550 QC to form a mixture comprising a hydrogen halide and a halogenated hydrocarbon, (c) at 330 Between -420GC

FeO(OH)分解鹵代烴而形成無鹵素烴類以及鹵素成分,(d)在 33 0-42(^(:之間藉由CaC03及/或Ca(OH)2吸收鹵化氫以及鹵素 0718-A21362TWF(N2);P10940035TW;shine 9 1305787 成$,(e)混合物在經過步驟(c)與(d)之後’轉變為氣態混合物 與第一油品,以及(f)將氣態混合物冷凝,得到第二油品。 【實施方式】 所明熱裂解反應就疋將固態或液態有機物質在缺氧環境 下加熱,促使有機物質化學鍵結斷裂而分解,部分有機物質之 ^子鏈會在適當環輕行她,形絲财機㈣。部分有機FeO(OH) decomposes halogenated hydrocarbons to form halogen-free hydrocarbons and halogen components, and (d) absorbs hydrogen halide and halogen 0718 between 33 0 and 42 (by CaC03 and/or Ca(OH)2). A21362TWF (N2); P10940035TW; shine 9 1305787 into $, (e) mixture after the steps (c) and (d) 'transformed into a gaseous mixture with the first oil, and (f) condense the gaseous mixture to obtain the first [Embodiment] The thermal cracking reaction shows that the solid or liquid organic matter is heated in an oxygen-deficient environment, causing the chemical bond of the organic substance to break and decompose, and the sub-chain of some organic substances will be lightly in the appropriate ring. She, the shape of the money machine (four). Partial organic

:質則保持低分子狀態’經過—系列的物理與化學反應之後, 生包括氣相之石炭氫化合物、水蒸氣、含固定石炭(Fked⑽⑽ ^、、炭(Char)與灰份之固體殘留物。若再經過適當的冷凝程 =乳相部分產品會以液態之油與水的型態出現。—般而言, =速率較㈣熱分解反應,所得趋含有鮮量的氣體產 ^加熱速雜慢者,其產物則以油及焦炭為主。以化學觀點 而吕,熱裂解反應可由下式表示: 揮發物+焦炭+灰分 有機物質(固態或液態)一^ 揮發物~~氣體+油+水 式。熱Λ解又可分為單純熱裂解與修正熱裂解兩種方 式。早純熱裂解是指在缺少*备/ 式進行熱魏,修正_解=或觀環境下,㈣接加熱方 接办刼士斗立丄 衣%疋指以適量空氣與燃料下,進行直 接加熱方式產生之熱裂解反廡 表2 %。表1說明兩種加熱方式的差異。 ----- 修正熱裂解(直接加熱) 單純熱裂解(間接加熱;) 熱傳效率較高 __ 需依賴中間熱傳物體如爐壁等,埶 0718-A2i362rWF(N2);Pt0940035TW;shine 10 1305787 ---____ 不需藉爐壁傳熱,最高溫度可達約 12〇〇°c 需藉爐壁傳熱,其材料要求較高, 最高只達約900qC 爐壁不會發生顯著的熱膨脹,保溫 :料内襯不會脫落 爐壁會發生顯著的熱膨脹,保溫及 耐火材内襯較易脫落 所有加熱用燃燒空氣及反應產生之 揮發氣體混合,因此煙氣處理設備 j雜較大 — 加熱用燃燒空氣及反應產生之揮發 氣體可分開處理,故後段煙氣處理 言史備較小 由於兩種熱裂解方式各具優劣,因此,可視實際需求選擇 肇 使用不同的裂解方式。本發明一實施例中的裂解槽是使用單純 熱裂解’在含有惰性氣體的環境中,透過間接加熱的方式來處 理廢棄塑膠。 以下說明本發明一實施例中塑膠裂解裝置的主要組成元 件。 請參照第2a圖,圖中所繪示的是本發明一實施例中的塑 膠裂解裝置200a,包括第一裂解槽201、第二裂解槽203、冷 凝器205、進料供應槽211、惰性氣體供應槽213、管線215 鲁 與217、以及閥219、221與223。其中,進料供應槽211連接 於第一裂解槽201,惰性氣體供應槽213連接於第一裂解槽 201,第一裂解槽201與第二裂解槽203之間以管線215相連, 第二裂解槽203與冷凝器205之間以管線217相連,閥219設 置於第二裂解槽203的底部,閥223與閥221分別設置於冷凝 器205的頂部與底部。 請參照第2b圖,圖中所繪示的是本發明一實施例中的塑 膠裂解裝置200b,其中,大部分的元件與塑膠裂解裝置200a 相同,於此不再贅述。不同之處,在於塑膠裂解裝置200b中 Π 0718-A21362TWF(N2);P10940035TW;shine 1305787 更包括吸收槽225’設置於第二裂解槽203與冷凝器205之間。 吸收槽225與第一裂解槽203之間以管線217a相連,吸收槽 225與冷凝器205之間以管線217b相連。 以下利用塑膠裂解裝置200a來說明本發明—實施例中裂 解塑膠的實施步驟。 首先,將例如氮氣等其他惰性氣體由惰性氣體供應槽213 通入苐一裂解槽201中約1〇分鐘,使槽中含有氮氣,之後停 止供應。須注意的是本發明不限於此,亦可在後續熱裂解的過 • 程中繼續供應氮氣。 其次’將含氣塑膠粉碎後置於進料供應槽211中,在常 壓或微負壓狀態下,以批次(Batch)方式供應至第一裂解槽2〇1 中,然本發明不限於此,亦可使用連續進料的方式供應塑膠進 料。含氯塑膠中可包括聚氯乙烯(PVC)。在本發明的一實施例 中,含氯塑膠中的氣含量以不超過1〇 wt%為較佳,且上述含 氯塑膠以顆粒狀或碎片狀為較佳。 之後,在300-550GC溫度下,較佳是420-48(^(:之間熔融 鲁 裂解位於第一裂解槽201中的含氯塑膠而形成一混合物,該混 &物中包括虱化氲、鼠代經(R-C1,或稱為有機氣化物)以及無 氯煙類,並藉由管線215將上述混合物傳送至第二裂解槽2〇3 中。含氯塑膠於熱裂解後主要生成氣態及液態產物,氣態產物 包括短鏈碳氫化合物’如Ha、CH4、C〇、c〇2等。在不同裂解 溫度中可能進行的反應及產物如下:100至2〇〇gc以脫水及乾 燥等物理變化為主;250〇C左右開始脫氧、脫氯、脫除結晶水、 產生C〇2及產生HC1氣體等反應;340QC以上時,脂肪族化合 0718-A2t362TWF(N2);P10940035TW;shine 12 1305787 物開始力解成CH4及其他較短鏈脂雜碳氫化合物,如碳數為 1〜5的炫類。 第二裂解槽203中容納有FeO(OH)及CaCCVCaC03作為 吸收劑’用來吸收氯化氫或氯成分以減少油品中的氯含量。 FeO(OH)作為觸媒’用以分解氯代烴中碳氫化合物與氯之間的 鍵結(R-C1鍵結),使裂解後的氯成分與吸收劑作用,生成 Ca(OCl)2 · 3H2〇或CaCl2 ·紐2〇等化合物,以更進一步地減 少油品中之氯含量。在本發明的另一實施例中,第二裂解槽2 〇 3 更谷納有Ca(OH)2,其亦作為吸收劑之用。上述步驟中所使用 的吸收劑為試藥級的CaC〇3,比表面積為15m2/g,由曰本 ShiraishiKogyo公司所提供。而上述步驟中所使用的觸媒為針 鐵礦a_Fe0(0H) ’其比表面積為86 m2/g,由曰本Toda Kogyo 么司所φς:供。在本發明的一實施例中,觸媒與吸收劑可自行製 造,亦可購自由日商TodaKogyo公司所提供的商品。 觸媒與吸收劑的製造方法如下。: The quality remains in a low molecular state 'after a series of physical and chemical reactions, including gas phase hydrogen carbide, water vapor, solid residue containing fixed carbon charcoal (Fked (10) (10) ^, char (Char) and ash. If the appropriate condensation process is followed, the product of the milk phase will appear as a liquid oil and water. In general, the rate is higher than that of the (four) thermal decomposition reaction, and the resulting gas contains a small amount of gas. The product is mainly oil and coke. From a chemical point of view, the thermal cracking reaction can be expressed by the following formula: volatiles + coke + ash organic matter (solid or liquid) - volatiles ~ ~ gas + oil + water The thermal enthalpy can be divided into two types: pure thermal cracking and modified thermal cracking. Early pure thermal cracking refers to the lack of *preparation / heat, the correction _ solution = or the environment, (four) connected to the heating刼 斗 斗 疋 疋 疋 疋 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以 以Direct heating) simple thermal cracking (indirect heating;) heat transfer Higher __ depends on intermediate heat transfer objects such as furnace walls, etc., 埶0718-A2i362rWF(N2); Pt0940035TW;shine 10 1305787 ---____ no need to borrow heat from the furnace wall, the maximum temperature can reach about 12〇〇°c The heat transfer by the furnace wall is required, and the material requirements are relatively high. The maximum wall temperature is only about 900qC. The furnace wall will not undergo significant thermal expansion. The heat preservation: the material lining will not fall off the furnace wall and significant thermal expansion will occur. The insulation and refractory lining will be better. It is easy to fall off all the combustion air for heating and the volatile gas generated by the reaction, so the flue gas treatment equipment is too large - the combustion air for heating and the volatile gas generated by the reaction can be treated separately, so the latter part of the flue gas treatment is smaller. The two thermal cracking methods have their own advantages and disadvantages. Therefore, different cracking methods can be selected according to actual needs. The cracking tank in one embodiment of the present invention uses simple thermal cracking in an environment containing an inert gas through indirect heating. The main components of the plastic cracking device in one embodiment of the present invention are described below. Please refer to FIG. 2a, which illustrates the present invention. The plastic cracking device 200a in the embodiment includes a first cracking tank 201, a second cracking tank 203, a condenser 205, a feed supply tank 211, an inert gas supply tank 213, a line 215 Lu and 217, and valves 219, 221 and 223. The feed supply tank 211 is connected to the first cracking tank 201, and the inert gas supply tank 213 is connected to the first cracking tank 201. The first cracking tank 201 and the second cracking tank 203 are connected by a line 215, and the second The cracking tank 203 and the condenser 205 are connected by a line 217, the valve 219 is disposed at the bottom of the second cracking tank 203, and the valve 223 and the valve 221 are respectively disposed at the top and the bottom of the condenser 205. Referring to Figure 2b, there is shown a plastic cracking apparatus 200b in an embodiment of the present invention, wherein most of the components are the same as the plastic cracking apparatus 200a, and will not be described herein. The difference is that in the plastic cracking device 200b, Π 0718-A21362TWF (N2); P10940035TW; shine 1305787 further includes an absorption tank 225' disposed between the second cracking tank 203 and the condenser 205. The absorption tank 225 is connected to the first cracking tank 203 by a line 217a, and the absorption tank 225 is connected to the condenser 205 by a line 217b. The plastic cracking apparatus 200a will be used hereinafter to explain the implementation steps of the splitting plastic in the present invention. First, another inert gas such as nitrogen gas is supplied from the inert gas supply tank 213 into the first cracking tank 201 for about 1 minute to contain nitrogen gas, and then the supply is stopped. It should be noted that the invention is not limited thereto, and it is also possible to continue supplying nitrogen during the subsequent thermal cracking. Next, the gas-containing plastic is pulverized and placed in the feed supply tank 211, and is supplied to the first cracking tank 2〇1 in a batch manner under a normal pressure or a micro-negative pressure state, but the invention is not limited thereto. Therefore, the plastic feed can also be supplied by continuous feeding. Polyvinyl chloride (PVC) may be included in the chlorine-containing plastic. In an embodiment of the invention, the gas content in the chlorine-containing plastic is preferably not more than 1% by weight, and the chlorine-containing plastic is preferably in the form of particles or chips. Thereafter, at a temperature of 300-550 GC, preferably 420-48 (^: melt-cracking the chlorine-containing plastic located in the first cracking tank 201 to form a mixture, and the mixture includes strontium telluride , the mouse passage (R-C1, or organic gasification) and the chlorine-free tobacco, and the above mixture is transferred to the second cracking tank 2〇3 by the line 215. The chlorine-containing plastic is mainly formed after the thermal cracking. Gaseous and liquid products, gaseous products include short-chain hydrocarbons such as Ha, CH4, C〇, c〇2, etc. Possible reactions and products at different cracking temperatures are as follows: 100 to 2 〇〇gc for dehydration and drying Such as physical changes; 250 ° C or so began to deoxidize, dechlorination, remove crystal water, produce C 〇 2 and produce HC1 gas and other reactions; above 340QC, aliphatic compound 0718-A2t362TWF (N2); P10940035TW; 1305787 begins to work into CH4 and other shorter chain aliphatic hydrocarbons, such as swarf with a carbon number of 1 to 5. The second cracking tank 203 contains FeO(OH) and CaCCVCaC03 as absorbents for absorption. Hydrogen chloride or chlorine to reduce the chlorine content of the oil. FeO(OH) is used as The catalyst 'is used to decompose the bond between the hydrocarbon and chlorine in the chlorinated hydrocarbon (R-C1 bond), so that the cracked chlorine component acts with the absorbent to form Ca(OCl) 2 · 3H 2 〇 or CaCl 2 a compound such as New Zealand to further reduce the chlorine content in the oil. In another embodiment of the present invention, the second cracking tank 2 〇3 has a Ca(OH)2, which is also absorbed. For the purpose of the agent, the absorbent used in the above steps is a reagent grade CaC〇3 with a specific surface area of 15 m2/g, which is supplied by Shiraishi Kogyo Co., Ltd., and the catalyst used in the above step is goethite a_Fe0. (0H) 'The specific surface area is 86 m2/g, which is supplied by T本Toda Kogyo 司 ς: In one embodiment of the present invention, the catalyst and the absorbent can be manufactured by themselves, and the Japanese business TodaKogyo can also be purchased. Products supplied by the company. The catalyst and absorbent are manufactured as follows.

CaCCV紛樹脂以90/10的重量比混合,混合攪拌期間添加 20 wt%的水以便造粒。添加酚樹脂是為了提高成品的機械強 度’所使用的酚樹脂之商品名為Bellpearl S890,由ICaneb〇公 司所提供。在500%且存在有惰性氣體的環境中將上述含有 CaC〇3、紛樹脂與水的混合物燒結1小時。之後,將cac〇3與 FeO(OH)以Fe/Ca莫耳比為35/65的比例混合,再添加l5wt% 的酚樹脂’並將該混合物在98Mpa的壓力下壓縮以造粒,顆粒 大小為25mm\|/*5mm。這些顆粒在800GC下碳化,然後粉碎, 篩選出粒徑為350-710um的顆粒,以供脫氯程序使用。 0718-A21362TWF(N2);P10940035TW;shine 1305787 第二裂解槽203中容納有FeO(OH)及CaC03,因此,將第 一裂解槽201中的混合物傳送至第二裂解槽203之後,該混合 物會在330-420oC的溫度下,較佳是在350-380¾的溫度下繼 續裂解’其中,觸媒Fe0(0H)將混合物中的氯代烴分解為無氣 經類以及氯成分’而吸收劑CaC03則將混合物中的氯化氫以及 氯成分吸收。因此,來自於第一裂解槽2〇1中的混合物在經過 裂%、分解與吸收之後’轉變為氣態混合物與液態油品(為方 便起見,在此稱為第一油品)’第一油品經由閥219排出,氣 • 態混合物則經由管線217輸送至冷凝器205冷凝,而得到另一 液態油品(在此稱為第二油品)^第二油品經由冷凝器2〇5底部 的閥221排出,而無法冷凝的氣體則經由閥223排出。在本發 明的一實施例中,第二油品中的氯含量較第一油品中的氯含量 為低。 含氣塑膠經由上述步驟轉變為液態油品的液化率可達55 wt%以上,所得的液態油品可作為化學原料或燃料使用,而混 合後之液態油品中的氯含量可降至〇.5wt%以下。 齡 卩上是利用塑膠裂解裝置麵來說解塑膠的實施步 驟。須注意的是本發明不限於此,在本發明的另一實施例中係 利用塑膠裂解裝置200b來裂解塑膠,亦即,自 排出的氣態混合物在傳送至冷凝器2〇5之前,會先㈣錄槽 225(請參照第2b圖)’將氣態混合物_所含的微量氯化氮或氯 成分更進-步地吸收,再傳送至冷凝器2〇5。吸收槽奶中可 包括CaC〇3及/或Ca(OH)2等吸收材料。此外,吸收槽225亦 可設置於第-裂解槽2〇1與第二裂解槽2〇3之間(圖中未緣示)。 0718-A21362TWF(N2) ;P 10940035TW:shine 1305787 以下特舉實施例與比較例進行說明。 比較例 將PVC/PE的塑膠碎粒以麵的重量比均勻混合,以抵 次方式供應至如第2a圖所示的塑縣解裝置聽中進行埶聲 解’第。-細曹观的裂解溫度為·。c,第二裂解槽的溫度 為350 C,而其餘裂解塑義實施步驟與條件均如前所述。須 注意岐味例的第二裂觸林含有_與吸收 實施例 將PVC/PE的塑膠碎粒以的重量比均勻混合,以批 次方式供應至如第2a圖所示的歸裂解裝置·a _進行熱裂 解’第-裂。解槽201的裂解溫度為48〇〇c,帛二裂解槽2〇3的 溫度為350QC,而其餘裂解塑膠的實施步驟與條件均如前所 述。第一裂解槽203容納有觸媒與吸收劑,觸媒為Fe〇(〇H), 吸收劑為CaC03與Ca(OH)2。 上述塑膝碎粒在經過實施例與比較例的熱裂解步驟後,所 得油品之密度、平均碳數、主要碳數分布及氯含量如表2所示。 表2 \ PVC/PE (wt%) 觸媒y吸收劑 密度 (g^cm3) 平均碳數 主要碳數分布 氯含量 (ppm) 比較例 1/100 無 0.77 14.1 n-C8 〜n-C10, 286.71 n-C16-n-C18 實施例 1/100 有 0.74 10.7 n-C6-n-C8. 9.26 ηΌ8 〜n-C10 由表2可知’實施例之塑膠碎粒在經過含有觸媒與吸收劑 0718-A21362TWF(N2);P10940035TW;shine 1305787 的塑膠裂解裝置後’平均碳數降低,氯含量亦明顯, 油品品質提升’更適合用於燃料或化學原料。此夕卜,·丄顯示 ,回收再利用’可延長塑膠中碳的使用生命週期,進轉由資 二氧化碳溫室效應的影響。除此之外,氣成分的減少=滅輕 對環境及生悲的危害’同時可避免廢塑膠因焚化而条低 奥辛等二次污染。此外,觸媒與吸㈣的使用有助 ^戴 裂解’減少裂解時間,進而節省能源之消耗。…,的The CaCCV resin was mixed at a weight ratio of 90/10, and 20 wt% of water was added during the mixing to pelletize. The phenol resin is added to increase the mechanical strength of the finished product. The phenol resin used is sold under the trade name Bellpearl S890, supplied by ICaneb. The above mixture containing CaC〇3, a resin and water was sintered in an environment of 500% and an inert gas for 1 hour. Thereafter, cac〇3 and FeO(OH) were mixed at a ratio of Fe/Ca molar ratio of 35/65, and then 15 wt% of phenol resin was added, and the mixture was compressed at 98 Mpa for granulation, particle size. It is 25mm\|/*5mm. The particles were carbonized at 800 GC and then pulverized to screen particles having a particle size of 350-710 um for use in a dechlorination procedure. 0718-A21362TWF(N2); P10940035TW; shine 1305787 The second cracking tank 203 contains FeO(OH) and CaC03, so after the mixture in the first cracking tank 201 is transferred to the second cracking tank 203, the mixture will be At a temperature of 330-420oC, it is preferred to continue cracking at a temperature of 350-3803⁄4. Among them, the catalyst Fe0(0H) decomposes the chlorinated hydrocarbon in the mixture into a gas-free and chlorine-containing component, and the absorbent CaC03 will Hydrogen chloride and chlorine components in the mixture are absorbed. Therefore, the mixture from the first cracking tank 2〇1 is 'transformed into a gaseous mixture and a liquid oil (for convenience, referred to herein as a first oil) after undergoing crack %, decomposition and absorption. The oil is discharged through the valve 219, and the gas mixture is sent to the condenser 205 via line 217 for condensation to obtain another liquid oil (referred to herein as the second oil). The second oil is passed through the condenser 2〇5. The valve 221 at the bottom is discharged, and the gas that cannot be condensed is discharged through the valve 223. In an embodiment of the invention, the chlorine content of the second oil is lower than the chlorine content of the first oil. The liquefaction rate of the gas-containing plastic converted into liquid oil through the above steps can reach 55 wt% or more, and the obtained liquid oil can be used as a chemical raw material or a fuel, and the chlorine content in the mixed liquid oil can be reduced to 〇. 5 wt% or less. Ageing is the implementation of plastics using a plastic cracker. It should be noted that the present invention is not limited thereto, and in another embodiment of the present invention, the plastic cracking device 200b is used to crack the plastic, that is, the self-exhausted gaseous mixture is first (four) before being sent to the condenser 2〇5. The recording tank 225 (please refer to FIG. 2b) 'takes the trace amount of nitrogen chloride or chlorine contained in the gaseous mixture _ further into the condenser and then transfers it to the condenser 2〇5. Absorbent materials such as CaC〇3 and/or Ca(OH)2 may be included in the absorption tank milk. Further, the absorption tank 225 may be disposed between the first cracking tank 2〇1 and the second cracking tank 2〇3 (not shown). 0718-A21362TWF (N2); P 10940035TW: shine 1305787 The following specific examples and comparative examples will be described. Comparative Example The plastic granules of PVC/PE were uniformly mixed in the weight ratio of the surface, and supplied to the squeaking solution as shown in Fig. 2a. - The cracking temperature of the fine Cao Guan is ·. c, the temperature of the second cracking tank is 350 C, and the remaining cracking and plasticizing steps and conditions are as described above. It should be noted that the second fissile forest of the astringent example contains _ and the absorption example uniformly mixes the weight ratio of the plastic granules of PVC/PE, and supplies it in batches to the lysis apparatus as shown in Fig. 2a. _ undergo thermal cracking 'first-cracking. The cracking temperature of the unblocking tank 201 is 48 〇〇c, and the temperature of the bismuth cracking tank 2〇3 is 350 QC, and the steps and conditions for the remaining cracked plastics are as described above. The first cracking tank 203 contains a catalyst and an absorbent, the catalyst is Fe〇 (〇H), and the absorbent is CaC03 and Ca(OH)2. The density, average carbon number, major carbon number distribution and chlorine content of the obtained oily product after the thermal cracking step of the above examples and comparative examples are shown in Table 2. Table 2 \ PVC/PE (wt%) Catalyst y Absorbent Density (g^cm3) Average Carbon Number Main Carbon Number Distribution Chlorine Content (ppm) Comparative Example 1/100 None 0.77 14.1 n-C8 ~n-C10, 286.71 n-C16-n-C18 Example 1/100 has 0.74 10.7 n-C6-n-C8. 9.26 ηΌ8 〜n-C10 It can be seen from Table 2 that the plastic granules of the examples pass through the catalyst and absorbent 0718- A21362TWF (N2); P10940035TW; Shine 1305787's plastic cracker, 'average carbon number reduction, chlorine content is also obvious, oil quality improvement' is more suitable for fuel or chemical raw materials. On the other hand, 丄 shows that recycling and recycling can extend the life cycle of carbon in plastics, and the impact of carbon dioxide greenhouse effect. In addition, the reduction of gas composition = the lightness of the environment and the sorrow of the sorrow, while avoiding the secondary pollution caused by the incineration of waste plastics. In addition, the use of catalyst and suction (4) helps to reduce cracking time and thus reduce energy consumption. …,of

雖然本發明已以較佳實施例揭露如上,然其並非用以 限定本發明,任何_此項技藝者,在不去除離本發明之 精神和範圍内,當可作更動與潤飾,因此本發明之^護範 圍當視後附之申請專利範圍所界定者為準。While the present invention has been described above in terms of the preferred embodiments thereof, it is not intended to limit the invention, and the present invention may be modified and retouched without departing from the spirit and scope of the invention. The scope of protection is subject to the definition of the scope of the patent application.

0718-A21362TWF(N2);P10940035TW;shine 16 1305787 【圖式簡單說明】 第1圖繪示的是傳統的塑膠裂解裝置。 第2a與2b圖係根據本發明實施例所繪示的塑膠裂解裝 【主要元件符號說明】 100、200a、200b〜塑膠裂解裝置; 101〜裂解槽; 105、205〜冷凝器; 111、211〜進料供應槽; 113〜氮氣供應槽; 116、215、217、217a、217ΐ>〜管線; 121、123、219、221、223〜閥; 201〜第一裂解槽; 203〜第二裂解槽; 213〜惰性氣體供應槽; 225〜吸收槽。 0718-A21362TWF(N2);P10940035TW;shine 170718-A21362TWF(N2); P10940035TW;shine 16 1305787 [Simple description of the drawing] Figure 1 shows a conventional plastic cracking device. 2a and 2b are a plastic cracking device according to an embodiment of the present invention. [Main component symbol description] 100, 200a, 200b~ plastic cracking device; 101~ cracking tank; 105, 205~ condenser; 111, 211~ Feed supply tank; 113~nitrogen supply tank; 116, 215, 217, 217a, 217ΐ>~ pipeline; 121, 123, 219, 221, 223~ valve; 201~ first cracking tank; 203~ second cracking tank; 213~ inert gas supply tank; 225~ absorption tank. 0718-A21362TWF(N2);P10940035TW;shine 17

Claims (1)

公告本 1305787 十、申請專利範圍: 1.一種塑膠裂解裝置,包括: 一第一裂解槽,用以將一含鹵素塑膠熔融裂解而形成 一混合物,其包括一‘鹵化氫與一鹵代烴: 一第二裂解槽,連接於該第一裂解槽,該第二裂解槽 用來容納FeO(OH)及CaC〇3,其中,FeO(OH)作為觸媒, 用以分解該鹵代烴而形成一無鹵素烴類以及一鹵素成分, CaC03作為第一吸收劑,用以吸收該鹵化氫以及該鹵素成 分;以及 一冷凝器,連接於該第二裂解槽。 2. 如申請專利範圍第1項所述之塑膠裂解裝置,其中 該第二裂解槽更用來容納Ca(0H)2,其作為第二吸收劑。 3. 如申請專利範圍第1項所述之塑膠裂解裝置,其中 該含鹵素塑膠為含氯塑膠,該鹵化氫為氯化氫,該_代烴 為氯代烴,該無齒素烴類為無氯烴類,該鹵素成分為氯成 分。 4. 如申請專利範圍第1項所述之塑膠裂解裝置,更包 括一吸收槽,設置於該第二裂解槽與該冷凝器之間。 5. 如申請專利範圍第1項所述之塑膠裂解裝置,更包 括一惰性氣體供應槽,連接於該第一裂解槽,該惰性氣體 供應槽是用以供應氮氣、氦氣或氖氣。 6. —種裂解塑膠的方法,包括: (a) 提供一含鹵素塑膠; (b) 在300-550GC之間裂解該含鹵素塑膠而形成一混 0718-A21362TWF(N2);P10940035TW;shine 18Announcement 1305787 X. Patent application scope: 1. A plastic cracking device comprising: a first cracking tank for melt cracking a halogen-containing plastic to form a mixture comprising a 'hydrogen halide and a halogenated hydrocarbon: a second cracking tank connected to the first cracking tank for containing FeO(OH) and CaC〇3, wherein FeO(OH) acts as a catalyst for decomposing the halogenated hydrocarbon to form a halogen-free hydrocarbon and a halogen component, CaC03 as a first absorbent for absorbing the hydrogen halide and the halogen component; and a condenser connected to the second cracking tank. 2. The plastic cracking apparatus of claim 1, wherein the second cracking tank is further adapted to contain Ca(0H)2 as a second absorbent. 3. The plastic cracking device according to claim 1, wherein the halogen-containing plastic is a chlorine-containing plastic, the hydrogen halide is hydrogen chloride, the hydrocarbon is a chlorinated hydrocarbon, and the dentate hydrocarbon is chlorine-free. Hydrocarbon, the halogen component is a chlorine component. 4. The plastic cracking device of claim 1, further comprising an absorption tank disposed between the second cracking tank and the condenser. 5. The plastic cracking apparatus of claim 1, further comprising an inert gas supply tank connected to the first cracking tank for supplying nitrogen, helium or neon. 6. A method of cracking a plastic comprising: (a) providing a halogen-containing plastic; (b) cracking the halogen-containing plastic between 300-550 GC to form a mixture 0718-A21362TWF(N2); P10940035TW; 1305787 合物,其包括一鹵化氫與一齒代烴; (C)在33(M200C之間藉由Fe0(0H)分解該鹵代烴而 形成一無鹵素烴類以及一齒素成分; (句在330-4200C之間藉由CaC〇3及/或Ca(〇JH)2吸收 該齒化風以及該齒素成分; ⑷該混合物在經過步驟(c)與(d)之後,轉變為一氣態 混合物與一第一油品;以及 (f)將該氣態混合物冷凝 得到一第二油品。 7·如”專利範圍第6項所述之裂解塑膠的方法 中該含i素塑膠中的齒素含量小於1〇 。 其 二:===_膠的方法,其 9.如申請專利範圍第6 該含鹵素塑膠為含氯塑膠, 為氯代烴,該無齒素烴類為 分0 項所述裂解塑膠的方法,其中 該鹵化氫為氯化氫,該齒代烴 無氯烴類,該鹵素成分為氯成 中二圍第6項所述之裂解塑膠的方法,其 甲,亥含鹵素塑膠是顆粒狀或碎片狀。 /、 η.如申請專利範圍第6項所述 中步卵)是在―c之間裂解該含时娜法’其 12.如申請專利範圍第6項所述 的 中步驟⑻更包括在含有情性氣體;2 塑膠。 兄r衣解该含鹵素 13.如申請專利範圍第6 項所述之裂解塑膠的方法, 其 〇718-A21362TWF(N2);P1 〇94〇〇35TW;Shine 19 ^05,787 中步驟(c)是在350-380oC下分解該鹵代烴。 14,如申請專利範圍第6項所述之裂解塑膠的方法,其 中步驟(d)是在35〇_38〇〇c下吸收該鹵化氫以及該_素成 分。 如申請專利範圍第6項所述之裂解塑膠的方法,其 該第-油品與該第二油品是作為化學原料或燃料使用。 中iL6·如巾請專利範圍第6項所述之裂解塑膠的方法,其 I低Γ弟二油品中的齒素含量較該第—油品中的幽素含量為 17’如中晴專利㈣第6項所述之裂解塑膠的方法,更 合該第一油品與該第二油品,且混合後油品中的齒 言含1為0.5 Wt%以下。a 1305787 compound comprising a hydrogen halide and a dentate hydrocarbon; (C) forming a halogen-free hydrocarbon and a dentate component by decomposing the halogenated hydrocarbon by Fe0(0H) at 33 (M200C; The toothed wind and the dentate component are absorbed between 330-4200C by CaC〇3 and/or Ca(〇JH)2; (4) the mixture is converted to a gaseous state after passing steps (c) and (d) a mixture of the first oil; and (f) condensing the gaseous mixture to obtain a second oil. 7. The method for cracking a plastic according to the method of claim 6 The content is less than 1 〇. The second method is: === _ glue method, 9. If the patent application scope is 6th, the halogen-containing plastic is a chlorine-containing plastic, which is a chlorinated hydrocarbon, and the dentate hydrocarbon is divided into 0 items. The method for cracking a plastic, wherein the hydrogen halide is hydrogen chloride, the toothed hydrocarbon is a chlorine-free hydrocarbon, and the halogen component is a method for cracking a plastic according to item 6 of the chlorine composition, wherein the halogen-containing plastic is Granular or fragmented. /, η. as described in the sixth paragraph of the patent application scope) is to cleave the inclusion between the "c" The step (8) as described in claim 6 of the patent application is further included in the case of containing a gas; 2 plastic. The method of dissolving the halogen as described in claim 6 of the patent application, 〇718-A21362TWF(N2); P1 〇94〇〇35TW; Shine 19^05,787, step (c) is to decompose the halogenated hydrocarbon at 350-380o C. 14. Cracked plastic as described in claim 6 The method of the present invention, wherein the step (d) is to absorb the hydrogen halide and the component of the bismuth at 35 〇 _ 38 〇〇 c. The method for cracking a plastic according to claim 6 of the invention, wherein the first oil The second oil is used as a chemical raw material or a fuel. The method for cracking plastic according to item 6 of the patent scope of the invention, the dentin content of the lower oil of the second oil is higher than that of the first oil. The method of cracking the plastic in the product is 17', as in the method of cracking the plastic according to item 6 of Zhongqing Patent (4), more suitable for the first oil and the second oil, and the mixed tooth in the oil contains 1 It is 0.5 Wt% or less. 0718-A21362TWF(N2) ;P10940035TW;shine 200718-A21362TWF(N2) ;P10940035TW;shine 20
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