TWI593722B - Granular rutile titanium dioxide catalyst and the decomposition of plastic methods - Google Patents

Granular rutile titanium dioxide catalyst and the decomposition of plastic methods Download PDF

Info

Publication number
TWI593722B
TWI593722B TW103104569A TW103104569A TWI593722B TW I593722 B TWI593722 B TW I593722B TW 103104569 A TW103104569 A TW 103104569A TW 103104569 A TW103104569 A TW 103104569A TW I593722 B TWI593722 B TW I593722B
Authority
TW
Taiwan
Prior art keywords
titanium oxide
rutile
catalyst
type titanium
copper
Prior art date
Application number
TW103104569A
Other languages
Chinese (zh)
Other versions
TW201500414A (en
Inventor
Yasuhiro Hosogi
Takayoshi Komiya
Original Assignee
Showa Denko Kk
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Showa Denko Kk filed Critical Showa Denko Kk
Publication of TW201500414A publication Critical patent/TW201500414A/en
Application granted granted Critical
Publication of TWI593722B publication Critical patent/TWI593722B/en

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • B01J35/612Surface area less than 10 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/06Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/72Copper
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/31Density
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/40Catalysts, in general, characterised by their form or physical properties characterised by dimensions, e.g. grain size
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/009Preparation by separation, e.g. by filtration, decantation, screening
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • B01J37/0203Impregnation the impregnation liquid containing organic compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • B01J37/088Decomposition of a metal salt
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/07Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of solid raw materials consisting of synthetic polymeric materials, e.g. tyres
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Catalysts (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Description

顆粒狀金紅石型氧化鈦觸媒以及塑膠之分解方法 Granular rutile titanium oxide catalyst and decomposition method of plastic

本發明係關於顆粒狀金紅石型氧化鈦觸媒及塑膠之分解方法。 The invention relates to a method for decomposing granular rutile-type titanium oxide catalyst and plastic.

分解觸媒意指分解有機物之觸媒,可列舉熱分解觸媒、氧化分解觸媒、光觸媒等。其中,已知使用氧化鈦之分解觸媒係廉價,化學穩定性優異,具有高觸媒活性,對人體無害等,而有用於分解觸媒(例如參照專利文獻1及2)。作為具體的利用方法,已知在使用氧化鈦之分解觸媒的存在下,藉由一邊紫外線照射廢塑膠一邊加熱,而將該廢塑膠氣化之方法(例如參照專利文獻3)。如此將氧化鈦作為分解觸媒使用而熱分解廢塑膠之方法,係為了藉由廢塑膠的熱分解而促進氣化,通常,於容器中一邊使載氣流通,一邊在攪拌下加熱氧化鈦及廢塑膠片,而熱分解廢塑膠,使熱分解生成物之分解氣體排出至容器外。因此,作為觸媒使用之氧化鈦粒子會磨損,會微粉化,與廢塑膠的熱分解生成氣體一起失去於容器外,故難以再利用,且為了得重複的觸媒性能,有不得不追加因為 磨損損失之量的觸媒之問題。又,伴隨氧化鈦粒子的微粉化,該粒度分布會變化,而有降低廢塑膠的分解效率之問題。 The decomposition catalyst means a catalyst for decomposing organic substances, and examples thereof include a thermal decomposition catalyst, an oxidative decomposition catalyst, and a photocatalyst. Among them, it is known that a decomposition catalyst using titanium oxide is inexpensive, has excellent chemical stability, has high catalytic activity, is harmless to the human body, and is used for decomposing a catalyst (see, for example, Patent Documents 1 and 2). As a specific method of use, a method of vaporizing the waste plastic by irradiating the waste plastic with ultraviolet rays in the presence of a decomposition catalyst of titanium oxide is known (for example, see Patent Document 3). The method of thermally decomposing the waste plastic by using titanium oxide as a decomposition catalyst is to promote vaporization by thermal decomposition of the waste plastic. Usually, the titanium oxide is heated under stirring while the carrier gas is passed through the container. The plastic sheet is scraped, and the waste plastic is thermally decomposed, and the decomposition gas of the thermal decomposition product is discharged to the outside of the container. Therefore, the titanium oxide particles used as a catalyst are abraded and micronized, and are lost to the outside of the container together with the thermal decomposition gas of the waste plastic, so that it is difficult to reuse, and in order to have repeated catalyst performance, it has to be added because The problem of the amount of catalyst lost by wear. Further, with the micronization of the titanium oxide particles, the particle size distribution changes, and there is a problem that the decomposition efficiency of the waste plastic is lowered.

尚且,作為高分解效率的分解觸媒,有提案1.2mm以上為1~50重量%,0.5~1.2mm為40~90重量%,0.5mm以下為1~20重量%之粒度分布的分解觸媒等(參照專利文獻4)。 Further, as a decomposition catalyst having a high decomposition efficiency, there is a proposal that a decomposition catalyst having a particle size distribution of 1.2 to 120% by weight is 0.5 to 1.2% by weight, 0.5 to 1.2 mm is 40 to 90% by weight, and 0.5 mm or less is 1 to 20% by weight. Etc. (refer to Patent Document 4).

〔先前技術文獻〕 [Previous Technical Literature] 〔專利文獻〕 [Patent Document]

[專利文獻1]特開2007-51263號公報 [Patent Document 1] JP-A-2007-51263

[專利文獻2]特開2006-346651號公報 [Patent Document 2] JP-A-2006-346651

[專利文獻3]特開2002-363337號公報 [Patent Document 3] JP-A-2002-363337

[專利文獻4]特開2005-205312號公報 [Patent Document 4] JP-A-2005-205312

然而,使用記載在專利文獻4的分解觸媒,特別是使用氧化鈦觸媒使廢塑膠熱分解時,還是藉由磨損分解觸媒會損失,且隨著時間分解效率會降低,故在工業實施還有進一步改進的餘地。 However, when the decomposition catalyst described in Patent Document 4 is used, in particular, when the waste plastic is thermally decomposed using a titanium oxide catalyst, the decomposition catalyst is lost by abrasion, and the decomposition efficiency decreases with time, so that it is industrially implemented. There is still room for further improvement.

於是,本發明的課題係在於提供一種高分解效率,且藉由分解反應中的磨損之觸媒損失少的氧化鈦觸媒,及使用該氧化鈦觸媒之塑膠的分解方法。 Accordingly, an object of the present invention is to provide a titanium oxide catalyst having a high decomposition efficiency and a small catalyst loss by abrasion in a decomposition reaction, and a decomposition method of a plastic using the titanium oxide catalyst.

本發明者為了達成上述目的而各種檢討的結果,發現具有特定粒度分布,且若持有一定以上之壓碎強度顆粒體的氧化鈦觸媒,則分解效率高,且藉由分解反應中的磨損之觸媒的損失少。本發明係基於上述發現而完成者。 As a result of various reviews in order to achieve the above object, the present inventors have found that a titanium oxide catalyst having a specific particle size distribution and holding a certain amount of crushing strength particles has high decomposition efficiency and wear by decomposition reaction. The catalyst has less loss. The present invention has been completed based on the above findings.

亦即,本發明係提供下述〔1〕~〔8〕者。 That is, the present invention provides the following [1] to [8].

〔1〕一種顆粒狀金紅石型氧化鈦觸媒,其粒徑1.2~1.5mm之顆粒的含量為80質量%以上,且其BET比表面積為0.1~0.4m2/g。 [1] A particulate rutile-type titanium oxide catalyst having a particle diameter of 1.2 to 1.5 mm of 80% by mass or more and a BET specific surface area of 0.1 to 0.4 m 2 /g.

〔2〕如上述〔1〕之顆粒狀金紅石型氧化鈦觸媒,其中,其體積密度為1.1~1.7g/mL,且其平均壓碎強度為10~70N。 [2] The particulate rutile-type titanium oxide catalyst according to the above [1], wherein the bulk density is 1.1 to 1.7 g/mL, and the average crushing strength is 10 to 70 N.

〔3〕如上述〔1〕或〔2〕的顆粒狀金紅石型氧化鈦觸媒,其中,造粒氧化鈦粉末後,以900~1,200℃燒成所得者。 [3] The particulate rutile-type titanium oxide catalyst according to the above [1] or [2], wherein the titanium oxide powder is granulated and then fired at 900 to 1,200 °C.

〔4〕如上述〔1〕~〔3〕的任一者之顆粒狀金紅石型氧化鈦觸媒,其中,金紅石型的結晶形態係含有78質量%以上。 [4] The particulate rutile-type titanium oxide catalyst according to any one of the above [1] to [3], wherein the rutile-type crystal form contains 78% by mass or more.

〔5〕如上述〔1〕~〔4〕的任一者之顆粒狀金紅石型氧化鈦觸媒,其中,其被承載銅氧化物。 [5] The particulate rutile-type titanium oxide catalyst according to any one of the above [1] to [4], wherein the particulate rutile-type titanium oxide catalyst is supported by a copper oxide.

〔6〕如上述〔5〕的顆粒狀金紅石型氧化鈦觸媒,對於除了銅氧化物之前述顆粒狀金紅石型氧化鈦觸媒100質 量份,以銅元素換算銅氧化物的承載量為1~15質量份。 [6] The particulate rutile-type titanium oxide catalyst according to the above [5], for the particulate rutile-type titanium oxide catalyst 100 other than copper oxide The amount of copper oxide supported by the copper element is 1 to 15 parts by mass.

〔7〕如上述〔1〕~〔6〕之任一者的顆粒狀金紅石型氧化鈦觸媒,其中,其係有機物的熱分解用。 [7] The particulate rutile-type titanium oxide catalyst according to any one of the above [1] to [6], which is used for thermal decomposition of an organic substance.

〔8〕一種塑膠的分解方法,其特徵為混合上述〔1〕~〔6〕之任一者的顆粒狀金紅石型氧化鈦觸媒與塑膠後加熱。 [8] A method for decomposing a plastic, characterized in that the particulate rutile-type titanium oxide catalyst of any one of the above [1] to [6] is mixed with a plastic and then heated.

根據本發明,可提供分解效率高,且分解反應中之磨損造成的觸媒損失少的顆粒狀金紅石型氧化鈦觸媒。進而,於承載有銅氧化物之顆粒狀金紅石型氧化鈦觸媒的情形,更提升分解效率。 According to the present invention, it is possible to provide a particulate rutile-type titanium oxide catalyst having high decomposition efficiency and little catalyst loss due to abrasion in the decomposition reaction. Further, in the case of a particulate rutile-type titanium oxide catalyst carrying copper oxide, the decomposition efficiency is further enhanced.

〔顆粒狀金紅石型氧化鈦觸媒〕 [Particulate rutile titanium oxide catalyst]

本發明之氧化鈦觸媒係粒徑1.2~1.5mm之顆粒的含量為80質量%以上,BET比表面積為0.1~0.4m2/g的顆粒狀金紅石型氧化鈦觸媒(以下有簡稱為金紅色石型氧化鈦觸媒的情形)。此處,顆粒意指造粒粒子,燒成後所得者。又,顆粒狀意指具有前述顆粒的形狀。 The titanium oxide catalyst of the present invention has a particle diameter of 1.2 to 1.5 mm and a content of particles of 80% by mass or more, and a granulated rutile-type titanium oxide catalyst having a BET specific surface area of 0.1 to 0.4 m 2 /g (hereinafter referred to as abbreviated as The case of gold red stone type titanium oxide catalyst). Here, the particles mean granulated particles, and those obtained after firing. Further, the granular shape means having the shape of the aforementioned particles.

本發明之金紅石型氧化鈦觸媒係亦可含其它的晶體形態,例如銳鈦礦型或板鈦礦型的結晶形態,有需要主要為金紅色型的結晶形態。具體而言,金紅石型的結晶形態係 佳為78質量%以上,較佳為80質量%以上,更佳為90質量%以上,進而再更佳為95質量%以上,特別是佳為使用含有實質上100質量%的氧化鈦觸媒。 The rutile-type titanium oxide catalyst system of the present invention may also contain other crystal forms, such as an anatase type or a brookite type crystal form, and a crystal form mainly requiring a gold-red type. Specifically, the rutile crystal form It is preferably 78% by mass or more, preferably 80% by mass or more, more preferably 90% by mass or more, still more preferably 95% by mass or more, and particularly preferably a titanium oxide catalyst containing substantially 100% by mass.

相較於銳鈦礦型氧化鈦及板鈦礦型氧化鈦,以及本發明之範圍外的金紅石型氧化鈦觸媒,本發明的金紅石型氧化鈦觸媒係分解效率優異。雖其原因尚不清楚,可推測金紅石型氧化鈦的存在下,可更高效率地進行從空氣中得氧,並將所得氧供給至有機物的反應。 The rutile-type titanium oxide catalyst of the present invention is superior in decomposition efficiency to the rutile-type titanium oxide catalyst other than the anatase-type titanium oxide and the brookite-type titanium oxide and the range of the present invention. Although the reason is not clear, it is presumed that in the presence of rutile-type titanium oxide, the reaction of obtaining oxygen from the air and supplying the obtained oxygen to the organic substance can be performed more efficiently.

本發明之金紅石型氧化鈦觸媒,其粒徑1.2~1.5mm之顆粒的含量係佳為85質量%以上,較佳為88質量%以上,更佳為90質量%以上。粒徑1.2~1.5mm之顆粒的含量為未達80質量%時,分解效率變差,又,耐磨損性不一定高。在粒徑1.2~1.5mm之顆粒的含量之上限值係未特別限制,通常,設為98質量%,很多的情形,往往是設為96質量%的傾向。 The rutile-type titanium oxide catalyst of the present invention preferably has a content of particles having a particle diameter of 1.2 to 1.5 mm of 85% by mass or more, preferably 88% by mass or more, and more preferably 90% by mass or more. When the content of the particles having a particle diameter of 1.2 to 1.5 mm is less than 80% by mass, the decomposition efficiency is deteriorated, and the abrasion resistance is not necessarily high. The upper limit of the content of the particles having a particle diameter of 1.2 to 1.5 mm is not particularly limited, and is usually 98% by mass, and in many cases, it tends to be 96% by mass.

又,BET比表面積係如前述,0.1~0.4m2/g為佳。若BET比表面積為該範圍,則會顯著產生粒子之粒成長及粒子間的薄片化,變成分解效率高,且耐磨損性高者。就同樣的觀點而言,BET比表面積係較佳為0.12~0.40m2/g,更佳為0.14~0.40m2/g。 Further, the BET specific surface area is preferably 0.1 to 0.4 m 2 /g as described above. When the BET specific surface area is in this range, grain growth of particles and flaking between particles are remarkably generated, and the decomposition efficiency is high and the abrasion resistance is high. From the same viewpoint, the BET specific surface area is preferably from 0.12 to 0.40 m 2 /g, more preferably from 0.14 to 0.40 m 2 /g.

本發明之金紅石型氧化鈦觸媒的體積密度係佳為1.1~1.7g/mL,較佳為1.3~1.7g/mL,更佳為1.3~1.6g/mL。若此範圍,則與有機物之接觸頻率變高,分解效率變高,且耐磨損性亦變高。進而本發明之金紅石 型氧化鈦觸媒的平均壓碎強度係佳為10~70N,較佳為13~70N,若此範圍,則耐磨損性優異。 The rutile-type titanium oxide catalyst of the present invention preferably has a bulk density of 1.1 to 1.7 g/mL, preferably 1.3 to 1.7 g/mL, more preferably 1.3 to 1.6 g/mL. When it is in this range, the contact frequency with an organic substance becomes high, decomposition efficiency becomes high, and abrasion resistance also becomes high. Further rutile of the present invention The average crushing strength of the titanium oxide catalyst is preferably from 10 to 70 N, preferably from 13 to 70 N, and in this range, the abrasion resistance is excellent.

未特別限制氧化鈦觸媒的製造方法,例如將四氯化鈦作為原料,藉由氣相法(藉由四氯化鈦與氧之氣相反應而得氧化鈦的方法)所得者為佳。以氣相法所得氧化鈦觸媒,係粒子徑為均勻之同時,因製造時經由高溫製程,而結晶性高。 The method for producing a titanium oxide catalyst is not particularly limited. For example, titanium tetrachloride is used as a raw material, and a gas phase method (a method of obtaining titanium oxide by a gas phase reaction between titanium tetrachloride and oxygen) is preferred. The titanium oxide catalyst obtained by the vapor phase method has a uniform particle diameter and a high crystallinity during production through a high-temperature process.

作為金紅石型氧化鈦觸媒,亦可使用市售氧化鈦觸媒調配。亦可使用將以氣相法所得氧化鈦的市售品(SDK.Co.jp製金紅石型氧化鈦「F-10」等)過篩後,設為BET比表面積為0.1~0.4m2/g,且粒徑1.2~1.5mm之顆粒的含量為80質量%以上之氧化鈦觸媒。 As the rutile-type titanium oxide catalyst, a commercially available titanium oxide catalyst can also be used. A commercially available product obtained by a vapor phase method (such as rutile-type titanium oxide "F-10" manufactured by SDK.Co.jp) may be used, and the BET specific surface area may be 0.1 to 0.4 m 2 / g, and the content of the particles having a particle diameter of 1.2 to 1.5 mm is 80% by mass or more of the titanium oxide catalyst.

又,市售品的氧化鈦觸媒之中,在使用比表面積大,金紅石型的結晶性係低者的情形,係進行燒成等而設為具有所定之比表面積及粒徑分布的氧化鈦即可。作為燒成溫度,佳為900~1,200℃,較佳為900~1,100℃。未特別限制燒成時間,通常,佳為10分鐘~5小時,較佳為30分鐘~3小時,更佳為45分鐘~2小時。 In addition, in the titanium oxide catalyst of the commercially available product, when the specific surface area is large and the rutile-type crystallinity is low, the oxidation is performed to have a predetermined specific surface area and particle size distribution. Titanium can be used. The firing temperature is preferably 900 to 1,200 ° C, preferably 900 to 1,100 ° C. The firing time is not particularly limited, and usually, it is preferably 10 minutes to 5 hours, preferably 30 minutes to 3 hours, more preferably 45 minutes to 2 hours.

〔承載有銅氧化物的顆粒狀金紅石型氧化鈦觸媒〕 [Particulate rutile-type titanium oxide catalyst carrying copper oxide]

藉由使本發明之金紅石型氧化鈦觸媒承載銅氧化物,進而可提升分解效率。尚且,銅氧化物係主要承載於觸媒表面。雖未特別限制銅氧化物,佳為氧化銅,較佳為二價氧化銅。 By allowing the rutile-type titanium oxide catalyst of the present invention to carry copper oxide, the decomposition efficiency can be improved. Moreover, the copper oxide is mainly carried on the surface of the catalyst. Although copper oxide is not particularly limited, it is preferably copper oxide, preferably divalent copper oxide.

於是,為了承載氧化銅,以下說明使用之銅化合物。 Thus, in order to carry copper oxide, the copper compound used will be described below.

(銅化合物) (copper compound)

為了在本發明之金紅石型氧化鈦觸媒承載銅氧化物而使用之銅化合物係亦可一價銅化合物,亦可二價銅化合物。又,亦可併用一價銅化合物與二價銅化合物。 The copper compound used for supporting the copper oxide in the rutile-type titanium oxide catalyst of the present invention may be a monovalent copper compound or a divalent copper compound. Further, a monovalent copper compound and a divalent copper compound may be used in combination.

作為一價銅化合物,雖未特別限制,可列舉選自氧化銅(I)、硫化銅(I)、碘化銅(I)、氯化銅(I)及氫氧化銅(I)之至少1種為佳。其中氧化銅(I)更佳。 The monovalent copper compound is not particularly limited, and may be at least 1 selected from the group consisting of copper (I) oxide, copper (I) sulfide, copper (I) iodide, copper (I) chloride, and copper (I) hydroxide. Kind is better. Among them, copper (I) oxide is more preferable.

作為二價銅化合物,雖未特別限制,可列舉選自氫氧化銅(II)、氧化銅(II)、氯化銅(II)、酢酸銅(II)、硫酸銅(II)、硝酸銅(II)、氟化銅(II)、碘化銅(II)及溴化銅(II)之至少1種為佳。其中硝酸銅(II)(Cu(NO3)2)更佳。 The divalent copper compound is not particularly limited, and examples thereof include copper (II) hydroxide, copper (II) oxide, copper (II) chloride, copper (II) citrate, copper (II) sulfate, and copper nitrate ( II), at least one of copper (II) fluoride, copper (II) iodide and copper (II) bromide is preferred. Among them, copper (II) nitrate (Cu(NO 3 ) 2 ) is more preferable.

作為銅化合物,佳為二價銅化合物,更佳為硝酸銅(II)。 As the copper compound, a divalent copper compound is preferred, and copper (II) nitrate is more preferred.

所使用銅化合物的平均粒徑係佳為0.5~100nm。若0.5nm以上,則結晶性變良好,並提升分解效率。若100nm以下,則具有(i)比表面積變大,分解效率優異,(ii)可良好的承載於氧化鈦等效果。就該觀點而言,銅化合物的平均粒徑係較佳為0.5~80nm,更佳為1~70nm,特佳為2~50nm。尚且,藉由使用電子顯微鏡觀察,而可確認粒子徑。此處,平均粒徑意指從50個粒子的大小求出的平均值。 The average particle diameter of the copper compound used is preferably from 0.5 to 100 nm. When it is 0.5 nm or more, the crystallinity becomes good, and the decomposition efficiency is improved. When the thickness is 100 nm or less, the (i) specific surface area is increased, the decomposition efficiency is excellent, and (ii) the effect of being supported on titanium oxide is good. From this point of view, the average particle diameter of the copper compound is preferably from 0.5 to 80 nm, more preferably from 1 to 70 nm, particularly preferably from 2 to 50 nm. Further, the particle diameter can be confirmed by observation with an electron microscope. Here, the average particle diameter means an average value obtained from the size of 50 particles.

對於金紅石型氧化鈦之銅化合物的使用量,係相對於除了銅氧化物之前述顆粒狀金紅石型氧化鈦觸媒100質量份,以銅元素換算銅氧化物的承載量為1~15質量份之方式調整即可。若1質量份以上,則藉由銅氧化物之承載展現良好的分解效率提升效果。又,若15質量份以下,則氧化鈦表面無法以銅氧化物大幅地被被覆,而良好地展現金紅石型氧化鈦之有機物分解機能。就同樣的觀點而言,相對於除了銅氧化物之前述顆粒狀金紅石型氧化鈦觸媒100質量份,以銅元素換算銅氧化物的承載量係較佳為1~12質量份,更佳為1~10質量份。 The amount of the copper compound of the rutile-type titanium oxide is 1 to 15 by mass in terms of the amount of the copper oxide in terms of copper element, based on 100 parts by mass of the particulate rutile-type titanium oxide catalyst other than the copper oxide. The method of adjustment can be. When it is 1 part by mass or more, the effect of enhancing the decomposition efficiency is exhibited by the bearing of the copper oxide. In addition, when it is 15 parts by mass or less, the surface of the titanium oxide cannot be largely coated with copper oxide, and the organic matter decomposition function of the red sapphire type titanium oxide is favorably exhibited. From the same viewpoint, the carrying amount of the copper oxide in terms of copper element is preferably from 1 to 12 parts by mass, more preferably 100 parts by mass of the particulate rutile-type titanium oxide catalyst other than the copper oxide. It is 1 to 10 parts by mass.

(銅氧化物的承載方法) (Method of carrying copper oxide)

對本發明的顆粒狀金紅石型氧化鈦觸媒之銅氧化物的承載方法係未特別限制,例如可列舉使顆粒狀金紅石型氧化鈦與銅化合物接觸後燒成的方法。 The method for supporting the copper oxide of the particulate rutile-type titanium oxide catalyst of the present invention is not particularly limited, and examples thereof include a method in which the particulate rutile-type titanium oxide is brought into contact with a copper compound and then fired.

作為顆粒狀金紅石型氧化鈦與銅化合物接觸的方法,將顆粒狀金紅石型氧化鈦浸漬於銅化合物溶液之方法為佳。此處,作為銅化合物溶液,銅化合物水溶液為佳。使接觸之際的溫度係佳為0~40℃,溫度為常溫之點係為了操作變為簡化而較佳。 As a method of contacting the particulate rutile-type titanium oxide with the copper compound, a method of immersing the particulate rutile-type titanium oxide in the copper compound solution is preferred. Here, as the copper compound solution, an aqueous copper compound solution is preferred. The temperature at the time of contact is preferably 0 to 40 ° C, and the point at which the temperature is normal temperature is preferable for the simplification of the operation.

將顆粒狀金紅石型氧化鈦浸漬於銅化合物溶液之後,使溶液蒸發後燒成。因此,溶液中之銅化合物係一旦變成全量係被摻入到氧化鈦。氧化鈦中的銅換算含量係藉由ICP(感應耦合等離子)發射光譜分析測量含有銅及鈦之 組成物而可定量。 After immersing the granular rutile-type titanium oxide in the copper compound solution, the solution was evaporated and then fired. Therefore, the copper compound in the solution is incorporated into the titanium oxide once it becomes a full amount. The content of copper in titanium oxide is measured by ICP (Inductively Coupled Plasma) emission spectroscopy to measure copper and titanium. The composition can be quantified.

燒成溫度係就所得金紅石型氧化鈦觸媒之分解效率的觀點而言,佳為250~600℃,較佳為250~550℃,更佳為300~550℃,特佳為300~500℃。雖然未特別限制燒成時間,通常,佳為30分鐘~10小時,較佳為1~8小時,更佳為3~8小時。 The firing temperature is preferably from 250 to 600 ° C, preferably from 250 to 550 ° C, more preferably from 300 to 550 ° C, and particularly preferably from 300 to 500, from the viewpoint of the decomposition efficiency of the rutile-type titanium oxide catalyst. °C. Although the firing time is not particularly limited, it is usually from 30 minutes to 10 hours, preferably from 1 to 8 hours, more preferably from 3 to 8 hours.

經如此操作,顆粒狀金紅石型氧化鈦觸媒中之銅化合物被轉換為銅氧化物,而可得經承載銅氧化物之顆粒狀金紅石型氧化鈦觸媒。經承載的銅氧化物係通常二價銅氧化物變為80質量%以上,佳為90質量%以上,較佳為95質量%以上,很多的情形,事實上佔100質量%。尚且,1價銅及2價銅的分析係使用如X射線吸收精細結構分析(XAFS)或電子自旋共振技術(ESR)的測量手法,並使用檢量線法,而可定量。 By doing so, the copper compound in the particulate rutile-type titanium oxide catalyst is converted into copper oxide, and a particulate rutile-type titanium oxide catalyst carrying a copper oxide can be obtained. The supported copper oxide system is usually 80% by mass or more, preferably 90% by mass or more, preferably 95% by mass or more, and in many cases, it accounts for 100% by mass. Further, the analysis of monovalent copper and divalent copper is carried out using a measurement method such as X-ray absorption fine structure analysis (XAFS) or electron spin resonance (ESR), and is quantified using a calibration curve method.

本發明之顆粒狀金紅石型氧化鈦亦可含有銅以外之其它金屬元素。作為其它金屬元素,可列舉例如鎢、鎵、鈮、鋯、鋁、鉬、錳、鉻等。其他亦可含有鹼金屬或鹼土金屬。 The particulate rutile-type titanium oxide of the present invention may also contain other metal elements than copper. Examples of the other metal element include tungsten, gallium, germanium, zirconium, aluminum, molybdenum, manganese, chromium, and the like. Others may also contain an alkali metal or an alkaline earth metal.

含有該金屬元素之情形,對於觸媒全體,該含量係佳為3質量%以下,較佳為1質量%以下,更佳為0.5質量%以下,特佳為0.1質量%以下。該金屬元素係有作為反應活性部位作用的情形,就抑制存在於氧化鈦之反應活性部位被失活的觀點而言,該含量係0.1質量%以下為佳。 In the case where the metal element is contained, the content is preferably 3% by mass or less, preferably 1% by mass or less, more preferably 0.5% by mass or less, and particularly preferably 0.1% by mass or less, based on the total amount of the catalyst. The metal element acts as a reactive site, and the content is preferably 0.1% by mass or less from the viewpoint of suppressing the deactivation of the reactive site present in the titanium oxide.

特別是作為有機物分解用的觸媒,例如作為 廢塑膠、橡膠、植物等熱分解用的觸媒,本發明之顆粒狀金紅石型氧化鈦優異。亦即,本發明亦提供混合上述本發明的顆粒狀金紅石型氧化鈦觸媒與塑膠後,藉由加熱之塑膠的分解方法。 Especially as a catalyst for decomposition of organic matter, for example, as The catalyst for thermal decomposition of waste plastics, rubber, plants, and the like is excellent in the particulate rutile-type titanium oxide of the present invention. That is, the present invention also provides a method for decomposing a plastic by heating the granular rutile-type titanium oxide catalyst and plastic of the present invention.

尚且,此處之熱分解意指在加熱至50℃以上的條件下引起之分解反應,藉由全體地氧化分解(氧化分解)的情形,或氧化分解一部分的情形亦包含在此「熱分解」。 Further, the thermal decomposition here means a decomposition reaction caused by heating to a temperature of 50 ° C or more, and the case of oxidative decomposition (oxidative decomposition) as a whole or a part of oxidative decomposition is also included in the "thermal decomposition". .

熱分解之際的溫度係依分解對象物而相異,適當地選擇即可。例如對象物為塑膠的情形係以佳為200~600℃,較佳為300~600℃,更佳為300~500℃熱分解。 The temperature at the time of thermal decomposition differs depending on the object to be decomposed, and may be appropriately selected. For example, the case where the object is a plastic is preferably 200 to 600 ° C, preferably 300 to 600 ° C, more preferably 300 to 500 ° C.

〔實施例〕 [Examples]

以下將本發明根據參考例、實施例及比較例具體的說明,但本發明未限定於該例。 Hereinafter, the present invention will be specifically described based on the reference examples, examples, and comparative examples, but the present invention is not limited to the examples.

尚且,將以各例得到之觸媒的物性及性能依示於以下的方法評價。 In addition, the physical properties and performance of the catalyst obtained in each example were evaluated by the following methods.

〔1.金紅石含量(金紅石含有率)〕 [1. Rutile content (rutile content)]

金紅石含量(質量%)係進行X線繞射測量,從對應銳鈦礦型結晶的峰高度(簡略Ha。),對應板鈦礦型結晶的峰高度(簡略Hb。),及對應金紅石型結晶的峰高度(Hr簡略。),基於下述式求出的值。 The rutile content (% by mass) is measured by X-ray diffraction, from the peak height of the corresponding anatase crystal (abbreviated Ha.), to the peak height of the brookite crystal (abbreviated Hb.), and the corresponding rutile. The peak height of the type crystal (Hr is abbreviated) is a value obtained based on the following formula.

[數1]金紅石含量(質量%)={Hr/(Ha+Hb+Hr)}×100 [Number 1] Rutile content (% by mass) = {Hr / (Ha + Hb + Hr)} × 100

〔2.BET比表面積〕 [2.BET specific surface area]

BET比表面積(m2/g)係使用Mountech Co.,Ltd.製全自動BET比表面積測量裝置「Macsorb,HM model-1208」測量。 The BET specific surface area (m 2 /g) was measured using a fully automatic BET specific surface area measuring device "Macsorb, HM model-1208" manufactured by Mountech Co., Ltd.

〔3.粒徑1.2~1.5mm之顆粒的含有率〕 [3. Content of particles with a particle size of 1.2 to 1.5 mm]

藉由以篩孔大小為1.14及1.45mm的篩搖篩,而篩分為微細粒子或粗大粒子,經考察該重量,測量粒徑1.2~1.5mm之顆粒的含有率(質量%)。 The sieve was divided into fine particles or coarse particles by a sieve having a mesh size of 1.14 and 1.45 mm, and the content (% by mass) of particles having a particle diameter of 1.2 to 1.5 mm was measured by examining the weight.

〔4.最小徑、中心徑、最大徑〕 [4. Minimum diameter, center diameter, maximum diameter]

使用標準篩並藉由篩分法,測量各粒徑的最小徑、中心徑及最大徑(mm)。 The minimum diameter, the center diameter, and the maximum diameter (mm) of each particle diameter were measured by a sieve using a standard sieve.

〔5.平均壓碎強度〕 [5. Average crush strength]

從使用木屋製作所製木屋式硬度計「WPF 1600-B」測量10次得到的值求出平均壓碎強度(N)。 The average crushing strength (N) was determined from a value obtained by measuring 10 times using a wooden house type hardness tester "WPF 1600-B" manufactured by a wooden house.

可判斷平均壓碎強度較強者,係堅硬且耐磨損性優異。 It can be judged that the average crushing strength is strong, and it is hard and excellent in abrasion resistance.

〔6.體積密度〕 [6. Bulk density]

將顆粒放進200mL量筒,經考察該重量,測量體積密度。 The pellets were placed in a 200 mL graduated cylinder and the bulk density was measured by examining the weight.

〔7.觸媒性能評價〕 [7. Catalyst performance evaluation]

於內部體積10L的耐熱玻璃(註冊商標)製反應管,在合成空氣(氮氣與氧氣的比率為8:2)下,混合氧化鈦顆粒觸媒200g及聚丙烯樹脂粒料0.02g,使升溫至400℃,10分鐘後在室溫下冷卻。藉由氣體分析裝置「PG-240」(HoribaCo.,Ltd製)測量產生之氣體種類及氣體濃度,評價分解能力。 In a reaction tube made of heat-resistant glass (registered trademark) having an internal volume of 10 L, 200 g of a titanium oxide particle catalyst and 0.02 g of a polypropylene resin pellet were mixed in a synthesis air (a ratio of nitrogen to oxygen of 8:2) to raise the temperature to After 400 minutes at 400 ° C, it was cooled at room temperature. The gas type and gas concentration generated were measured by a gas analyzer "PG-240" (manufactured by Horiba Co., Ltd.) to evaluate the decomposition ability.

可判斷一氧化碳(CO)少,且二氧化碳(CO2)較多者係分解效率高。 It can be judged that carbon monoxide (CO) is small, and those with more carbon dioxide (CO 2 ) have high decomposition efficiency.

〔8.反應中的觸媒的磨損率之算出方法〕 [8. Method for calculating the wear rate of the catalyst in the reaction]

前述觸媒性能評價時,使用篩孔大小1.14mm的篩,求出將反應後的觸媒分篩之際的穿過篩之觸媒重量,從該重量及反應前的觸媒量之比率,算出反應中的觸媒磨損率。 In the evaluation of the catalyst performance, a sieve having a mesh size of 1.14 mm was used, and the ratio of the weight of the catalyst passing through the sieve at the time of screening the catalyst after the reaction, and the ratio of the amount of the catalyst before the reaction, was determined. The catalyst wear rate in the reaction was calculated.

[數2]磨損率={(反應前的觸媒重量-上述分篩後之篩上的觸媒重量)/反應前的觸媒重量}×100 [Number 2] Wear rate = {(activator weight before reaction - catalyst weight on the sieve after the above sieve) / catalyst weight before reaction} × 100

〔9.銅承載量的測量〕 [9. Measurement of copper bearing capacity]

於氟酸溶液中加熱得到的試料使全部溶解,藉由ICP發射光譜分析定量抽出液。 The sample obtained by heating in a hydrofluoric acid solution was completely dissolved, and the extract was quantitatively analyzed by ICP emission spectrometry.

<實施例1> <Example 1>

藉由造粒機造粒一次粒子徑為約30nm之銳鈦礦型的氧化鈦粉末,1,000℃下燒成90分鐘後,而得到顆粒狀金紅石型氧化鈦觸媒。藉由以篩孔大小為1.14及1.45mm的篩分篩得到的觸媒,得到所定粒徑的顆粒狀金紅石型氧化鈦觸媒。藉由以篩分篩,得到1.2~1.5mm之顆粒的重量為90%的顆粒。 The anatase-type titanium oxide powder having a primary particle diameter of about 30 nm was granulated by a granulator, and calcined at 1,000 ° C for 90 minutes to obtain a particulate rutile-type titanium oxide catalyst. A particulate rutile-type titanium oxide catalyst having a predetermined particle size is obtained by a catalyst obtained by a sieve sieve having a mesh size of 1.14 and 1.45 mm. By sieving the sieve, particles having a weight of from 1.2 to 1.5 mm of 90% were obtained.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<實施例2> <Example 2>

使用1次粒子徑為約60nm之銳鈦礦型氧化鈦粉末以外,與實施例1同樣地操作,而得到顆粒狀金紅石型氧化鈦觸媒。 A particulate rutile-type titanium oxide catalyst was obtained in the same manner as in Example 1 except that an anatase-type titanium oxide powder having a primary particle diameter of about 60 nm was used.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<實施例3> <Example 3>

將燒成溫度設為900℃以外,與實施例1同樣地操作,而得到顆粒狀金紅石型氧化鈦觸媒。 The pelletized rutile-type titanium oxide catalyst was obtained in the same manner as in Example 1 except that the firing temperature was changed to 900 °C.

求出該觸媒的金紅石含量、BET比表面積、粒徑分 布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 Calculate the rutile content, BET specific surface area, and particle size of the catalyst. The cloth, the particle size, the average crushing strength, the bulk density, and the wear rate of the catalyst in the reaction, and the results thereof are shown in Table 1 together with the results of the catalyst performance evaluation.

<實施例4> <Example 4>

將燒成溫度設為1,100℃以外,與實施例1同樣地操作,而得到顆粒狀金紅石型氧化鈦觸媒。 The pelletized rutile-type titanium oxide catalyst was obtained in the same manner as in Example 1 except that the firing temperature was changed to 1,100 °C.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<實施例5> <Example 5>

將於實施例1得到的顆粒狀金紅石型氧化鈦觸媒100g浸漬於0.094mol/L的硝酸銅水溶液0.5L,100℃下使蒸發乾燥後,藉由以400℃燒成5小時,而得到對於除了銅氧化物的顆粒狀金紅石型氧化鈦觸媒100質量份之氧化銅(II)的承載量(銅元素換算)為3質量份之顆粒狀金紅石型氧化鈦觸媒。 100 g of the particulate rutile-type titanium oxide catalyst obtained in Example 1 was immersed in 0.5 L of a 0.094 mol/L copper nitrate aqueous solution, and after evaporating and drying at 100 ° C, it was baked at 400 ° C for 5 hours. The amount of copper (II) oxide (100% by mass) of the particulate rutile-type titanium oxide catalyst in addition to the copper oxide is 3 parts by mass of the particulate rutile-type titanium oxide catalyst.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<實施例6> <Example 6>

使用0.313mol/L的硝酸銅以外,與實施例5同樣地操作,而得到對於除了銅氧化物的顆粒狀金紅石型氧化鈦 觸媒100質量份之氧化銅(II)的承載量(銅元素換算)為10質量份之顆粒狀金紅石型氧化鈦觸媒。 A granular rutile-type titanium oxide other than copper oxide was obtained in the same manner as in Example 5 except that 0.313 mol/L of copper nitrate was used. The amount of copper (II) oxide (100% by mass) of the catalyst is 10 parts by mass of the particulate rutile-type titanium oxide catalyst.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<比較例1> <Comparative Example 1>

實施例1中未進行篩分以外同樣地操作,而得到顆粒狀金紅石型氧化鈦觸媒。 In the same manner as in Example 1, except that the sieving was carried out, a particulate rutile-type titanium oxide catalyst was obtained.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<比較例2> <Comparative Example 2>

藉由造粒機造粒一次粒子徑為約30nm之銳鈦礦型的氧化鈦粉末,800℃下燒成90分鐘後,而得到顆粒狀金紅石型氧化鈦觸媒,但未進行分篩。 The anatase-type titanium oxide powder having a primary particle diameter of about 30 nm was granulated by a granulator, and calcined at 800 ° C for 90 minutes to obtain a particulate rutile-type titanium oxide catalyst, but the sieve was not sieved.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<比較例3> <Comparative Example 3>

藉由造粒機造粒一次粒子徑為約30nm之銳鈦礦型的氧化鈦粉末,700℃下燒成90分鐘後,而得到顆粒狀金紅 石型氧化鈦觸媒。藉由以篩孔大小為1.14及1.45mm的篩分篩得到觸媒,得到所定粒徑的顆粒狀金紅石型氧化鈦觸媒。藉由以篩分篩,而得到1.2~1.5mm之顆粒的重量為91%的顆粒。 The anatase-type titanium oxide powder having a primary particle diameter of about 30 nm was granulated by a granulator, and calcined at 700 ° C for 90 minutes to obtain a granular gold red. Stone type titanium oxide catalyst. A particulate rutile-type titanium oxide catalyst having a predetermined particle diameter was obtained by obtaining a catalyst by a sieve sieve having a mesh size of 1.14 and 1.45 mm. By sieving the sieve, particles having a weight of 91% to 1.5 mm were obtained.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<比較例4> <Comparative Example 4>

藉由造粒機造粒一次粒子徑為約30nm之銳鈦礦型的氧化鈦粉末,750℃下燒成90分鐘後,而得到顆粒狀金紅石型氧化鈦觸媒。藉由以篩孔大小為1.14及1.45mm的篩分篩得到觸媒,而得到所定粒徑的顆粒狀金紅石型氧化鈦觸媒。藉由以篩分篩,而得到1.2~1.5mm之顆粒的重量為91%的顆粒。 The anatase-type titanium oxide powder having a primary particle diameter of about 30 nm was granulated by a granulator, and calcined at 750 ° C for 90 minutes to obtain a particulate rutile-type titanium oxide catalyst. A particulate rutile-type titanium oxide catalyst having a predetermined particle diameter was obtained by obtaining a catalyst by a sieve sieve having a mesh size of 1.14 and 1.45 mm. By sieving the sieve, particles having a weight of 91% to 1.5 mm were obtained.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

<比較例5> <Comparative Example 5>

藉由造粒機造粒一次粒子徑為約30nm之銳鈦礦型的氧化鈦粉末,1,300℃下燒成90分鐘後,而得到顆粒狀金紅石型氧化鈦觸媒。藉由以篩孔大小為1.14及1.45mm的篩分篩得到觸媒,而得到所定粒徑的顆粒狀金紅石型氧化 鈦觸媒。藉由以篩分篩,而得到1.2~1.5mm之顆粒的重量為93%的顆粒。 The anatase-type titanium oxide powder having a primary particle diameter of about 30 nm was granulated by a granulator, and calcined at 1,300 ° C for 90 minutes to obtain a particulate rutile-type titanium oxide catalyst. By obtaining a catalyst by a sieve sieve having a mesh size of 1.14 and 1.45 mm, a granular rutile oxidation of a predetermined particle size is obtained. Titanium catalyst. By sieving the sieve, particles having a weight of 93% of particles of 1.2 to 1.5 mm were obtained.

求出該觸媒的金紅石含量、BET比表面積、粒徑分布、粒徑、平均壓碎強度、體積密度,反應中之觸媒的磨損率,並將其結果與觸媒性能評價的結果一起示於表1。 The rutile content, BET specific surface area, particle size distribution, particle diameter, average crushing strength, bulk density, and the wear rate of the catalyst in the reaction were determined, and the results were compared with the results of the catalyst performance evaluation. Shown in Table 1.

根據表1的實施例1~4,本發明之顆粒狀金紅石型氧化鈦觸媒係分解效率高,且耐磨損性優異。進而根據實施例5及6,可知承載有銅氧化物之顆粒狀金紅石型氧化鈦觸媒,係將耐磨損性維持在高水準的狀態下,可更提高分解效率。 According to Examples 1 to 4 of Table 1, the particulate rutile-type titanium oxide catalyst of the present invention has high decomposition efficiency and excellent abrasion resistance. Further, according to Examples 5 and 6, it is understood that the particulate rutile-type titanium oxide catalyst carrying the copper oxide maintains the wear resistance at a high level, and the decomposition efficiency can be further improved.

另一方面,粒徑1.2~1.5mm之顆粒含量少的比較例1及2之觸媒的情形時,可知有進一步改善分解效率的餘地。以低溫燒成的比較例3及4之觸媒的情形時,觸媒的磨損顯著,再度進行觸媒反應之際,變成需要新增加觸媒的添加,在經濟上不利。 On the other hand, in the case of the catalysts of Comparative Examples 1 and 2 having a small particle diameter of 1.2 to 1.5 mm, it was found that there was room for further improvement of the decomposition efficiency. In the case of the catalysts of Comparative Examples 3 and 4 which were fired at a low temperature, the wear of the catalyst was remarkable, and when the catalyst reaction was again performed, the addition of a new catalyst was required, which was economically disadvantageous.

另一方面,以高溫燒成的比較例5之觸媒的情形時,觸媒的比表面積變成太小,而磨損率變低,且亦降低分解效率。 On the other hand, in the case of the catalyst of Comparative Example 5 which was fired at a high temperature, the specific surface area of the catalyst became too small, the wear rate became low, and the decomposition efficiency was also lowered.

尚且,作為產生氣體監控一氧化碳及二氧化碳,一氧化碳係有毒氣體,期望排出少,但完全氧化體之二氧化碳係排出較多為佳。因此,為了實際使用,一氧化碳的比率少,且二氧化碳的比率較多為佳。就該觀點而言,可判斷較比較例1~5的觸媒,實施例1~6的觸媒為更優異的觸媒。 Further, as a gas generating gas, carbon monoxide and carbon dioxide are monitored, and carbon monoxide is a toxic gas, and it is desirable to discharge less, but it is preferable to discharge more carbon dioxide in the complete oxidant. Therefore, for practical use, the ratio of carbon monoxide is small, and the ratio of carbon dioxide is preferably high. From this point of view, the catalysts of Comparative Examples 1 to 5 can be judged, and the catalysts of Examples 1 to 6 are more excellent catalysts.

Claims (8)

一種顆粒狀金紅石型氧化鈦觸媒,其粒徑1.2~1.5mm之顆粒的含量為80質量%以上,且其BET比表面積為0.1~0.4m2/g。 A particulate rutile-type titanium oxide catalyst having a particle diameter of 1.2 to 1.5 mm of 80% by mass or more and a BET specific surface area of 0.1 to 0.4 m 2 /g. 如申請專利範圍第1項之顆粒狀金紅石型氧化鈦觸媒,其中,其體積密度為1.1~1.7g/ml,且其平均壓碎強度為10~70N。 For example, the granular rutile-type titanium oxide catalyst of the first aspect of the patent application has a bulk density of 1.1 to 1.7 g/ml and an average crushing strength of 10 to 70 N. 如申請專利範圍第1或2項的顆粒狀金紅石型氧化鈦觸媒,其中,造粒氧化鈦粉末後,以900~1,200℃燒成所得者。 A granular rutile-type titanium oxide catalyst according to claim 1 or 2, wherein the titanium oxide powder is granulated and then fired at 900 to 1,200 °C. 如申請專利範圍第1或2項之顆粒狀金紅石型氧化鈦觸媒,其中,金紅石型的結晶形態係含有78質量%以上。 The particulate rutile-type titanium oxide catalyst according to claim 1 or 2, wherein the rutile-type crystal form is 78% by mass or more. 如申請專利範圍第1或2項之顆粒狀金紅石型氧化鈦觸媒,其中,其被承載銅氧化物。 A particulate rutile-type titanium oxide catalyst according to claim 1 or 2, wherein the particulate rutile-type titanium oxide catalyst is loaded with a copper oxide. 如申請專利範圍第5項的顆粒狀金紅石型氧化鈦觸媒,對於除了銅氧化物之前述顆粒狀金紅石型氧化鈦觸媒100質量份,以銅元素換算銅氧化物的承載量為1~15質量份。 In the particulate rutile-type titanium oxide catalyst of the fifth aspect of the invention, the amount of copper oxide in terms of copper element is 1 for 100 parts by mass of the particulate rutile-type titanium oxide catalyst other than the copper oxide. ~15 parts by mass. 如申請專利範圍第1或2項的顆粒狀金紅石型氧化鈦觸媒,其中,其係有機物的熱分解用。 The particulate rutile-type titanium oxide catalyst according to claim 1 or 2, wherein the particulate rutile-type titanium oxide catalyst is used for thermal decomposition of an organic substance. 一種塑膠的分解方法,其特徵為混合申請專利範圍第1~6項中任一項的顆粒狀金紅石型氧化鈦觸媒與塑膠後加熱。 A method for decomposing a plastic, characterized in that the granular rutile-type titanium oxide catalyst of any one of the first to sixth aspects of the patent application is mixed with a plastic and then heated.
TW103104569A 2013-02-14 2014-02-12 Granular rutile titanium dioxide catalyst and the decomposition of plastic methods TWI593722B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2013026662 2013-02-14

Publications (2)

Publication Number Publication Date
TW201500414A TW201500414A (en) 2015-01-01
TWI593722B true TWI593722B (en) 2017-08-01

Family

ID=51354001

Family Applications (1)

Application Number Title Priority Date Filing Date
TW103104569A TWI593722B (en) 2013-02-14 2014-02-12 Granular rutile titanium dioxide catalyst and the decomposition of plastic methods

Country Status (3)

Country Link
JP (1) JPWO2014125995A1 (en)
TW (1) TWI593722B (en)
WO (1) WO2014125995A1 (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101827664A (en) * 2007-10-19 2010-09-08 草津电机株式会社 Catalyst circulating waste plastic/organic matter decomposition apparatus and decomposition system
CN102137717A (en) * 2008-08-20 2011-07-27 堺化学工业株式会社 Catalyst and method for pyrolysis of organic substances and method for manufacturing such catalyst
CN102137724A (en) * 2008-08-20 2011-07-27 草津电机株式会社 Method of decomposing waste plastic/organic material using titanium oxide granule with optimal particle property

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005187794A (en) * 2003-12-03 2005-07-14 Kaoru Fujimoto Method for liquefying waste plastic and inorganic oxide particle for liquefying the waste plastic
JP4602690B2 (en) * 2004-04-21 2010-12-22 堺化学工業株式会社 Disassembly method of waste plastic
KR101508016B1 (en) * 2006-04-19 2015-04-06 쿠사츠 일렉트릭 컴퍼니 리미티드 Method of decomposing waste plastic/organic substance, decomposition apparatus, and decomposition system
TW200916215A (en) * 2007-07-05 2009-04-16 Panasonic Corp Method of recovering valuable materials from waste household electrical appliance

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101827664A (en) * 2007-10-19 2010-09-08 草津电机株式会社 Catalyst circulating waste plastic/organic matter decomposition apparatus and decomposition system
CN102137717A (en) * 2008-08-20 2011-07-27 堺化学工业株式会社 Catalyst and method for pyrolysis of organic substances and method for manufacturing such catalyst
CN102137724A (en) * 2008-08-20 2011-07-27 草津电机株式会社 Method of decomposing waste plastic/organic material using titanium oxide granule with optimal particle property

Also Published As

Publication number Publication date
TW201500414A (en) 2015-01-01
WO2014125995A1 (en) 2014-08-21
JPWO2014125995A1 (en) 2017-02-02

Similar Documents

Publication Publication Date Title
Dong et al. Tuning oxygen vacancy concentration of MnO2 through metal doping for improved toluene oxidation
Liao et al. Catalytic properties of manganese oxide polyhedra with hollow and solid morphologies in toluene removal
Schumann et al. Synthesis and characterisation of a highly active Cu/ZnO: Al catalyst
Zhao et al. Tailored design of high–stability CoMn1. 5Ox@ TiO2 double–wall nanocages derived from Prussian blue analogue for catalytic combustion of o–dichlorobenzene
JP5638746B2 (en) Catalyst and method for pyrolyzing organic matter and method for producing such a catalyst
Li et al. Fluorine-doped TiO2 powders prepared by spray pyrolysis and their improved photocatalytic activity for decomposition of gas-phase acetaldehyde
Gonzalez-Prior et al. Oxidation of chlorinated alkanes over Co 3 O 4/SBA-15 catalysts. Structural characterization and reaction mechanism
EP3689823A1 (en) Composite oxide, metal-supporting material and ammonia synthesis catalyst
Nagvenkar et al. Zinc oxide as a solid acid catalyst for esterification reaction
Znaiguia et al. Toward longer life catalysts for dehydration of glycerol to acrolein
CN101365535A (en) Low temperature ammonia remediation catalysts
Zhang et al. Promotion of H2O2 decomposition activity over β-MnO2 nanorod catalysts
Kwon et al. Influence of attrition milling on V/Ti catalysts for the selective oxidation of ammonia
Cha et al. Enhanced low-temperature NH3-SCR activity of a V2O5/TiO2 composite prepared via chemical vapor condensation and impregnation method
Lukic et al. Decoupling the Effects of High Crystallinity and Surface Area on the Photocatalytic Overall Water Splitting over β‐Ga2O3 Nanoparticles by Chemical Vapor Synthesis
Wan et al. Investigation on the structure-activity relationship of Nb2O5 promoting CeO2-CrOx-Nb2O5 catalysts for 1, 2-dichloroethane elimination
Jia et al. Efficient visible-light-responsive photocatalyst: hybrid TiO2-Ag3PO4 nanorods
Weng et al. Niobium phosphates as new highly selective catalysts for the oxidative dehydrogenation of ethane
JP7246101B2 (en) ELECTRONIC OR HYDRIDE ION SORTING OR DESTROYING COMPOSITIONS, TRANSITION METAL SUPPORTS AND CATALYSTS, AND THEIR RELATED USE
Zhang et al. Selective oxidation of propylene to acrolein over silver-promoted hexagonal molybdates and derivative Ag/Ag2Mo4O13/α-MoO3 composites
TWI593722B (en) Granular rutile titanium dioxide catalyst and the decomposition of plastic methods
JP6914114B2 (en) Metal oxide catalyst and its production method and acrylonitrile production method using it
JP5707841B2 (en) Method for producing fluidized bed catalyst and method for producing acrylonitrile
Li et al. C, N co-doping promoted mesoporous Au/TiO 2 catalyst for low temperature CO oxidation
Guo et al. Synthesis of Ag, Pd-loaded Bi2WO6 and its photocatalytic activities

Legal Events

Date Code Title Description
MM4A Annulment or lapse of patent due to non-payment of fees