JP3030626B2 - Activated carbon made from leather waste and its production method - Google Patents
Activated carbon made from leather waste and its production methodInfo
- Publication number
- JP3030626B2 JP3030626B2 JP10051317A JP5131798A JP3030626B2 JP 3030626 B2 JP3030626 B2 JP 3030626B2 JP 10051317 A JP10051317 A JP 10051317A JP 5131798 A JP5131798 A JP 5131798A JP 3030626 B2 JP3030626 B2 JP 3030626B2
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- Japan
- Prior art keywords
- activated carbon
- leather
- leather waste
- gas
- temperature
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Description
【0001】[0001]
【発明の属する技術分野】本発明は皮革廃材の利用技術
に係り、特にこれらの皮革廃材を製造原料として得られ
る活性炭およびその製造方法に関する。[0001] The present invention relates to a technology for utilizing leather waste, and more particularly to activated carbon obtained by using such leather waste as a raw material and a method for producing the same.
【0002】[0002]
【従来の技術および解決すべき課題】皮革製品の素材と
してのは原皮は用途に応じて各部分に裁断分割され夫々
靴やかばん等の製品の形態に加工されるが、これらの製
造工程で裁断屑等の皮革廃材が生じる。また原皮の中で
もきずや色むらのあるいわゆるB級品、C級品について
は在庫として残される割合いも多く最終的には廃材とし
て処分される場合があり、全体として原皮に対して約2
0%の割合いで皮革廃材が生じているものと考えられて
いる。2. Description of the Related Art As a raw material of a leather product, a raw leather is cut and divided into parts according to the use and processed into products such as shoes and bags, respectively. Leather waste such as waste is generated. Also, among the raw hides, so-called B-grade products and C-grade products, which have flaws or uneven color, are often left in stock, and may eventually be disposed of as waste material.
It is considered that leather waste is generated at a rate of 0%.
【0003】現在我国における天然皮革の取扱い高は海
外からの輸入や国内産のものを含めて年間約1000万
m2 以上になるものと推定され、したがって皮革廃材の
年間の排出量もこれにともなって極めて大量に上るもの
となる。このような皮革廃材はその材料の性状により、
他の廃棄物のように、たとえば紙をパルプとして再生
し、又は金属材料製品から構成金属を分離回収して資源
として再利用する方法が全く見出されておらず、現状で
は単に産業廃棄物として処理されている。また皮革廃材
はたん白質を含む動物の皮膚組織からなるためその処理
方法にも自ずから制約があり、最終的には焼却炉によっ
て処分すべきことになるが、焼却時に皮革廃材から発生
する排ガスについても種々の問題のあることが考えら
れ、そのための適切な処理方法が求められている。At present, the handling volume of natural leather in Japan, including imports from overseas and domestic ones, is estimated to be about 10 million m 2 or more per year. Accordingly, the annual amount of leather waste material is also increased accordingly. Very large numbers. Such leather waste material depends on the properties of the material,
As with other waste, for example, no method has been found to recycle paper as pulp, or to separate and recover constituent metals from metal material products and reuse them as resources. Is being processed. In addition, since leather waste consists of animal skin tissue including protein, its treatment method is naturally limited, and it must ultimately be disposed of by incinerators. It is thought that there are various problems, and an appropriate processing method for that is required.
【0004】本発明者等はこのような現状から皮革廃材
の適切な処理について検討した結果、天然皮革が相当量
の炭素成分を含有することに着目し、皮革廃材を単に従
来のように埋設又は燃焼焼却する代わりに炭化炉中で炭
化させて有用な用途のある活性炭とする可能性について
研究した。[0004] The present inventors have studied the appropriate treatment of leather waste material from such a situation, and as a result, have noticed that natural leather contains a considerable amount of carbon components. The possibility of carbonization in a carbonization furnace instead of combustion and incineration into activated carbon with useful applications was studied.
【0005】活性炭は主としてヤシ殻や石炭等から得ら
れる吸着剤として多くの産業分野で利用されており、近
年では大気中や水中の汚染物質の除去等の環境保全の用
途ならびに、防臭、脱臭および水処理などの用途にも需
要が増加しており、産業界や市民生活中で広く用いられ
ている。活性炭およびその製造原料のほとんどは海外か
らの輸入に依存しており、供給が安定しているとはいえ
ない。現在未利用のまゝ廃棄、焼却されている大量の皮
革廃材をこのような活性炭の原料として用いることがで
きれば、天然資源の再利用や活性炭の製造コストの低下
に寄与すると共に、皮革廃材自体の廃棄処理費用が節減
され、さらに焼却による大気中の二酸化炭素等の増大が
その分抑止されて環境保全の上からも有意義であると考
えられる。Activated carbon is used in many industrial fields mainly as an adsorbent obtained from coconut shells, coal, etc. In recent years, activated carbon has been used for environmental protection such as removal of pollutants in the air and water, as well as for deodorization, deodorization, and the like. Demand is increasing for applications such as water treatment, and it is widely used in industry and civil life. Most of activated carbon and its raw materials depend on imports from overseas, and the supply is not stable. If a large amount of leather waste that is currently unused and discarded or incinerated can be used as a raw material for such activated carbon, it will contribute to the reuse of natural resources and lower the production cost of activated carbon, as well as the use of leather waste itself. It is considered that waste disposal costs are reduced, and an increase in atmospheric carbon dioxide and the like due to incineration is suppressed correspondingly, which is significant from the viewpoint of environmental protection.
【0006】ところで活性炭の特徴的な性質である吸着
能は出発原料の材質によって異なり、またこのような吸
着能を効果的に得るための製造方法や条件も個々の原料
について異なっている。しかし植物性せん維によって構
成されるヤシ殻等の従来の原料とは著しく性状の異なる
動物性の皮革廃材を活性炭の原料として用いることは従
来全く知られていなかった。したがって、皮革廃材を原
料として活性炭の製造を行うに当たっては、先ず実用上
充分な吸着能を有する活性炭が得られる可能性自体の予
見が困難なことに加えて、この原料について最適な処理
方法や処理条件を新たに確立せねばならない課題があ
る。本発明者等は皮革廃材からの活性炭の製造について
研究および実験を重ね、その具体的な製造工程および製
造条件を明らかにして本発明を完成するに至った。[0006] Incidentally, the adsorptive capacity, which is a characteristic property of activated carbon, differs depending on the material of the starting material, and the production method and conditions for effectively obtaining such adsorptive power also differ for each raw material. However, it has not been known at all heretofore to use animal leather waste material having significantly different properties from conventional materials such as coconut shells composed of vegetable fibers as a raw material for activated carbon. Therefore, when producing activated carbon using leather waste as a raw material, it is difficult to foresee the possibility of obtaining an activated carbon having sufficient adsorption capacity for practical use. There are issues that require new conditions to be established. The present inventors have repeated research and experiments on the production of activated carbon from leather waste, and have clarified the specific production steps and production conditions to complete the present invention.
【0007】[0007]
【0008】前記本発明の課題は、皮革廃材を不活性ガ
ス中において300℃〜400℃の温度で炭化し、次い
で800〜850℃の温度で0.5〜1時間ガス賦活化
することを特徴とする皮革廃材を原料とする活性炭の製
造方法によって解決される。An object of the present invention is to carbonize waste leather in an inert gas at a temperature of 300 ° C. to 400 ° C., and then activate the gas at a temperature of 800 to 850 ° C. for 0.5 to 1 hour. The problem is solved by a method for producing activated carbon using leather waste as a raw material.
【0009】[0009]
【発明の好ましい実施態様】以下本発明を好ましい具体
的な実施態様についてさらに説明する。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be further described with reference to preferred specific embodiments.
【0010】(原料)本発明による活性炭は動物性の天
然皮革の廃材を炭化して得られるものであり、原料とな
る皮革廃材としては皮革製品を製造する際の裁断工程等
からの廃材や長時間の保管によって変質したB、C級品
から生じる皮革廃材等任意のものが用いられる。原皮の
種類や製品の表面加工処理に用いられた染料その他の薬
剤等は炭化物としての活性炭の収率や吸着性能にはほと
んど影響しない。(Raw material) The activated carbon according to the present invention is obtained by carbonizing animal natural leather waste material. Examples of the leather waste material as a raw material include waste material obtained from a cutting process or the like in the production of leather products. Arbitrary materials such as leather waste materials generated from B and C grade products that have been altered by storage over time are used. The type of raw hide and the dyes and other chemicals used in the surface treatment of the product have little effect on the yield and adsorption performance of activated carbon as a carbide.
【0011】(原料の炭化)本発明の皮革廃材を原料と
する活性炭は本発明の方法を実施する下記のフロ−に示
す工程によって製造される。(Carbonization of Raw Material) Activated carbon using the waste leather material of the present invention as a raw material is produced by the steps shown in the following flow for carrying out the method of the present invention.
【0012】 (フロー) 皮革廃材 → (炭化炉) → 炭化物 → (賦活炉) → 皮革活性炭 不活性ガス中、 炭酸ガス; 300℃以上 不活性ガス+炭酸ガス; で炭化 不活性ガス+水蒸気; 800℃〜850℃ で賦活(Flow) Leather waste material → (Carburizing furnace) → Carbide → (Activating furnace) → Leather activated carbon Carbon dioxide gas in an inert gas; 300 ° C. or more Inert gas + carbon dioxide gas; Inert gas + steam; 800 Activated at ℃ to 850 ℃
【0013】まず原料としての皮革廃材たとえばタンニ
ンなめし皮の廃材100gを適宜小片に裁断し、これら
を炭化炉で不活性ガスの気流中で加熱処理して炭化させ
る。熱重量分析により皮革廃材は約270℃の温度で熱
分解を起こし、300℃の温度で最初のピーク(分解速
度最大)が発生することが分かった。このように皮革廃
材を炭化処理するには、通常の原料からの活性炭の製造
工程におけるよりも低い温度で炭化が進行する。First, 100 g of leather waste material as a raw material, for example, tannin tanned leather waste material is cut into small pieces as appropriate, and these are heat-treated in an inert gas stream in a carbonization furnace to carbonize. Thermogravimetric analysis showed that the leather waste material was thermally decomposed at a temperature of about 270 ° C., and the first peak (maximum decomposition rate) was generated at a temperature of 300 ° C. In order to carbonize leather waste in this way, carbonization proceeds at a lower temperature than in the process of producing activated carbon from ordinary raw materials.
【0014】実際の実験では次工程における賦活化の機
構をより明確に解析するために炭化を窒素気流中におい
て原料中の揮発分がほぼ完全に除去されるような温度
(約800℃)で2時間行なったところ24%の収率で
炭化物が得られた。実用上の炭化炉では前記のように約
300℃以上の温度、特に約400℃程度で炭化させる
ことが好ましく、炭化は従来の原料を用いた場合の炭化
温度よりもかなり低い温度で行われる。これは主として
材料を構成する細胞質が植物性せん維材料ではセルロー
ス細胞壁で外側をかこまれているのに対し、動物性の天
然皮革ではこのような明確なセルロース外壁がなくリポ
たんぱく等を主成分とする原形質膜のみによって覆われ
ていることによるものと思われる。In an actual experiment, in order to more clearly analyze the mechanism of activation in the next step, carbonization was carried out at a temperature (about 800 ° C.) at which volatiles in the raw material were almost completely removed in a nitrogen stream. After 24 hours, carbide was obtained in a yield of 24%. As described above, in a practical carbonization furnace, it is preferable to carbonize at a temperature of about 300 ° C. or more, particularly about 400 ° C., and carbonization is performed at a temperature considerably lower than the carbonization temperature when a conventional raw material is used. This is mainly due to the fact that the cytoplasm constituting the material is surrounded by cellulose cell walls in plant fibrous materials, whereas natural animal leather does not have such a clear cellulose outer wall and contains lipoprotein as the main component. This is probably due to the fact that it is covered only by the plasma membrane.
【0015】(ガス賦活化)原料皮革廃材からの所定量
の炭化物を次いで前記フロ−に示すように賦活炉中で窒
素ガスと炭酸ガスとの混合ガスからなる賦活ガスを用い
て加熱処理することによって賦活化する。この賦活化に
よって炭化物に形成される大きな吸着有効表面と微細な
孔における毛管凝縮とによって吸着量が増加し吸着性能
が向上する。(Gas Activation) A predetermined amount of carbides from the raw material leather waste is then subjected to heat treatment in an activation furnace using an activation gas comprising a mixed gas of nitrogen gas and carbon dioxide gas as shown in the flow. Activated by Due to this activation, a large adsorption effective surface formed on the carbide and capillary condensation in the fine pores increase the adsorption amount and improve the adsorption performance.
【0016】活性炭を製造する際の炭化物の賦活処理と
しては一般にガス賦活法および薬品賦活法があるが、本
発明の実施例ではガス賦活法を採用した。またガス賦活
化に用いられるガスとしては窒素と炭酸ガスとの混合物
を用いたが、炭酸ガスを単独で用いてもよく、その他水
蒸気等も利用でき、これらと不活性ガス(窒素)との混
合物を用いてもよい。炭酸ガスを用いた場合の炭化物と
の反応は基本的には次式で示される。In general, there are a gas activating method and a chemical activating method for activating a carbide when producing activated carbon. In the embodiment of the present invention, the gas activating method is employed. As the gas used for gas activation, a mixture of nitrogen and carbon dioxide gas was used. However, carbon dioxide gas may be used alone, or steam or the like may be used, and a mixture of these and an inert gas (nitrogen) may be used. May be used. The reaction with carbide when using carbon dioxide gas is basically represented by the following equation.
【0017】[0017]
【化1】C+CO2 =2CO−40.8kcalEmbedded image C + CO 2 = 2CO-40.8 kcal
【0018】炭化物の賦活化における熱分析の結果を与
える図1に示すように、皮革の炭化物は750℃以上の
温度から分解してガス化反応が開始され約900℃で分
解が終了する。この場合の反応速度はガス濃度に依存す
る。本発明の実施例では賦活温度を800℃(1H
r)、850℃(0.5Hr、1Hr)および900℃
(0.5Hr、1Hr)に夫々設定し、賦活化ガスとし
て窒素と炭酸ガスとを混合して用い(300/200:
400/100ml/min)、炭化物試料を電気炉中
で炉温度を10℃/minで上昇させた後夫々所定温度
で保持して賦活を終了しその後すみやかに冷却した。As shown in FIG. 1, which gives the results of thermal analysis in the activation of carbides, the carbides of leather decompose at a temperature of 750 ° C. or higher, a gasification reaction starts, and the decomposition ends at about 900 ° C. The reaction rate in this case depends on the gas concentration. In the embodiment of the present invention, the activation temperature is set to 800 ° C. (1H
r), 850 ° C. (0.5 Hr, 1 Hr) and 900 ° C.
(0.5 Hr, 1 Hr), and nitrogen and carbon dioxide are mixed and used as the activation gas (300/200:
(400/100 ml / min), the carbide sample was heated in an electric furnace at a rate of 10 ° C./min, and then maintained at a predetermined temperature to terminate the activation, and then cooled immediately.
【0019】(吸着性能および収率)このようにして8
00〜900℃の賦活化温度で得られた皮革廃材からの
活性炭の炭化物に対する収率(%)および吸着性能(I
mg/Cg)を下記表1示す。(Adsorption performance and yield)
Yield (%) and adsorption performance (I) of activated carbon from leather waste obtained at an activation temperature of 00 to 900 ° C.
mg / Cg) is shown in Table 1 below.
【0020】[0020]
【表1】 [Table 1]
【0021】表1に示すように、よう素の吸着量は賦活
処理の温度と時間にに影響され、800℃〜900℃で
の処理によって吸着能および収率について概ね良好な結
果がえられた。吸着量については800℃〜850℃の
温度で活性炭1g当り約500〜600mgのよう素吸
着量(mg/g)が得られ、特に800℃の温度によっ
て処理した場合には約600mg/gの高い吸着能が得
られた。このように、皮革炭化物の賦活は植物せん維を
原料とする場合よりも低い温度で行うことが有効であ
る。また賦活温度900℃で吸着量の低下が著しくなる
が、これは過度な賦活処理によって炭化物表面に形成さ
れた微細孔が崩壊することおよび吸着を妨げる灰分量が
増加することによるものと考えられる。As shown in Table 1, the amount of iodine adsorbed was affected by the temperature and time of the activation treatment, and the treatment at 800 ° C. to 900 ° C. gave generally good results in terms of adsorption capacity and yield. . Regarding the amount of adsorption, an iodine adsorption amount (mg / g) of about 500 to 600 mg per 1 g of activated carbon is obtained at a temperature of 800 ° C. to 850 ° C., and particularly as high as about 600 mg / g when treated at a temperature of 800 ° C. Adsorption capacity was obtained. Thus, it is effective to activate the leather carbide at a lower temperature than when vegetable fibrous is used as a raw material. At 900 ° C., the amount of adsorption is remarkably reduced. This is considered to be due to the collapse of micropores formed on the carbide surface due to excessive activation and the increase in the amount of ash that hinders adsorption.
【0022】室内の消臭、防臭および水中の夾雑物の吸
着除去のために木炭を用いることは従来から行われてい
るが、これら通常の木炭のよう素吸着量は約200mg
/g程度である。これに対して皮革を原料とする活性炭
の前記吸着能は約2.5〜3倍程度大きく室内や調度品
の収納空間および身のまわり製品の消臭や防臭には実用
上充分な効果を有している。Conventionally, charcoal has been used for deodorizing and deodorizing indoors and for removing and adsorbing impurities in water. However, the amount of adsorbed iodine of these ordinary charcoals is about 200 mg.
/ G. On the other hand, the adsorption capacity of activated carbon made from leather is about 2.5 to 3 times that of the activated carbon, which is practically sufficient for deodorizing and deodorizing the room, the storage space for furniture, and the surrounding products. doing.
【0023】[0023]
【発明の効果】本発明の実施例による活性炭は、従来再
生利用の用途が見出せないまゝに廃棄処理されておりそ
の焼却についても問題を生じる懸念のあった皮革廃材を
原料として活用して種々の用途有用な活性炭を低コスト
で製造することができるので環境保護および資源の再利
用の点で優れた効果を与える。The activated carbon according to the embodiment of the present invention has been discarded before the use for recycling can not be found, and various kinds of activated carbon are used as raw materials by using leather waste material, which has a problem in incineration. Since useful activated carbon can be produced at a low cost, it has an excellent effect in terms of environmental protection and resource recycling.
【図1】本発明の製造方法による炭化物の賦活化におけ
る熱重量分析の結果を示すグラフである。FIG. 1 is a graph showing the results of thermogravimetric analysis in the activation of carbide by the production method of the present invention.
───────────────────────────────────────────────────── フロントページの続き (56)参考文献 東独特許237298(DD,A) ソ連国特許発明1838235(SU,A) スペイン特許2018379(ES,A6) Entropie 98(1981)p108 −111 (58)調査した分野(Int.Cl.7,DB名) C01B 31/08 - 31/14 CA(STN) WPI(DIALOG)──────────────────────────────────────────────────続 き Continuation of the front page (56) Reference East German Patent 237298 (DD, A) USSR Patent Invention 1838235 (SU, A) Spanish Patent 2018379 (ES, A6) Entropie 98 (1981) p108-111 (58) Search Field (Int.Cl. 7 , DB name) C01B 31/08-31/14 CA (STN) WPI (DIALOG)
Claims (3)
℃〜400℃の温度で炭化し、次いで800〜850℃
の温度で0.5〜1時間ガス賦活化することを特徴とす
る皮革廃材を原料とする活性炭の製造方法。1. A method in which leather waste material is placed in an inert gas for 300 hours.
Carbonization at a temperature between 400C and 400C, then 800-850C
A method for producing activated carbon using leather waste material as a raw material, wherein gas activation is carried out at a temperature of 0.5 to 1 hour.
請求項1記載の製造方法。2. The method according to claim 1, wherein carbon dioxide gas is used for the gas activation treatment.
ガスまたは水蒸気との混合物を用いる請求項1記載の製
造方法。3. The method according to claim 1, wherein a mixture of an inert gas and carbon dioxide or steam is used for the gas activation treatment.
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JP10051317A JP3030626B2 (en) | 1998-02-18 | 1998-02-18 | Activated carbon made from leather waste and its production method |
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JP10051317A JP3030626B2 (en) | 1998-02-18 | 1998-02-18 | Activated carbon made from leather waste and its production method |
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Publication Number | Publication Date |
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JPH11228120A JPH11228120A (en) | 1999-08-24 |
JP3030626B2 true JP3030626B2 (en) | 2000-04-10 |
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Families Citing this family (4)
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CN1317433C (en) * | 2005-02-07 | 2007-05-23 | 苏立暖 | Process for making leather facing fabric suede and products made thereby |
CN108658071B (en) * | 2017-03-31 | 2021-02-19 | 北京化工大学 | Biomass porous carbon taking chromium skin as raw material and preparation method and application thereof |
CN109589881A (en) * | 2018-12-13 | 2019-04-09 | 南京工业大学 | Method for preparing nitrogen-doped porous carbon-based aerogel from leather waste and application |
CN109678134A (en) * | 2019-01-25 | 2019-04-26 | 齐鲁工业大学 | A method of porous carbon materials are prepared using the waste in aldehyde-plant combination tannage process hides |
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1998
- 1998-02-18 JP JP10051317A patent/JP3030626B2/en not_active Expired - Fee Related
Non-Patent Citations (1)
Title |
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Entropie 98(1981)p108−111 |
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JPH11228120A (en) | 1999-08-24 |
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