JP3027763B2 - Activated carbon for recovery of organic halogenated solvents - Google Patents

Activated carbon for recovery of organic halogenated solvents

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Publication number
JP3027763B2
JP3027763B2 JP2158401A JP15840190A JP3027763B2 JP 3027763 B2 JP3027763 B2 JP 3027763B2 JP 2158401 A JP2158401 A JP 2158401A JP 15840190 A JP15840190 A JP 15840190A JP 3027763 B2 JP3027763 B2 JP 3027763B2
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JP
Japan
Prior art keywords
activated carbon
meq
granular activated
recovery
total
Prior art date
Legal status (The legal status 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 status listed.)
Expired - Fee Related
Application number
JP2158401A
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Japanese (ja)
Other versions
JPH0450110A (en
Inventor
栄治 田中
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Kuraray Chemical Co Ltd
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Kuraray Chemical Co Ltd
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Publication of JPH0450110A publication Critical patent/JPH0450110A/en
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Expired - Fee Related legal-status Critical Current

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  • Separation Of Gases By Adsorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Carbon And Carbon Compounds (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は有機ハロゲン系溶剤回収用粒状活性炭及びそ
の製法に関するもので、特に、空気などのガス中に含ま
れる有機ハロゲン系溶剤を吸着・脱着工程によって回収
するために使用するものである。
Description: TECHNICAL FIELD The present invention relates to a granular activated carbon for recovering an organic halogen-based solvent and a method for producing the same, and particularly to adsorbing and desorbing an organic halogen-based solvent contained in a gas such as air. It is used for recovery in the process.

〔従来の技術〕[Conventional technology]

空気などのガス中に含まれる有機ハロゲン系溶剤の蒸
気を吸着して回収するため、以前から種々の活性炭が使
用されていた。しかし、これらの有機ハロゲン系溶剤は
分解され易いため、活性炭表面に吸着されたとき、或い
は、脱着の際、高温スチームや空気を導入したとき、活
性炭の細孔内でこれらの溶剤が分解される。このため塩
素やフッ素などのハロゲンイオンが生成し、吸着装置を
腐食する原因となる。耐食性がある材質とするために
は、例えば、チタン等を用いる必要があり、非常に高価
なため、実用上問題があった。
Various activated carbons have been used for a long time to adsorb and recover the vapor of an organic halogen-based solvent contained in a gas such as air. However, since these organic halogen-based solvents are easily decomposed, these solvents are decomposed in the pores of the activated carbon when they are adsorbed on the activated carbon surface or when high temperature steam or air is introduced during desorption. . For this reason, halogen ions such as chlorine and fluorine are generated and cause corrosion of the adsorption device. In order to use a material having corrosion resistance, for example, it is necessary to use titanium or the like, which is very expensive, and thus has a practical problem.

近年、多量のフロン、トリクレンなどのハロゲン系溶
剤がクリーニング、電子部品の洗浄などに用いられてい
る。しかし最近、大気圏のオゾン層破壊の原因としてフ
ロンが取り上げられ、大気中に放出することが禁止され
た。代替フロンとして有機塩素系溶剤やアルコール等の
使用が計画されている。これらの有機塩素系溶剤、フロ
ンおよびフロン代替溶剤としてトリクロロエタン、トリ
クロロエチレン、塩化メチレン、四塩化炭素等の溶剤の
回収には活性炭が主に用いられてきたが、尚性能的に多
くの問題があった。
In recent years, a large amount of halogen-based solvents such as chlorofluorocarbon and trichlene have been used for cleaning, cleaning of electronic parts, and the like. Recently, however, chlorofluorocarbon has been raised as a cause of ozone depletion in the atmosphere, and its emission into the atmosphere has been banned. The use of organic chlorinated solvents, alcohols, etc. is being planned as a substitute for CFCs. Activated carbon has been mainly used to recover trichloroethane, trichloroethylene, methylene chloride, carbon tetrachloride and other solvents as these organic chlorine-based solvents, chlorofluorocarbons and chlorofluorocarbon substitutes, but there were still many problems in performance. .

〔発明が解決しようとする課題〕[Problems to be solved by the invention]

フロン、トリクロロエタンなどのハロゲン系溶剤は分
解し易く、特に活性炭に吸着された状態においては、活
性炭の触媒性及び脱着時に加えられる熱あるいはスチー
ムの作用によって容易に分解し、ハロゲンイオンを発生
する。このため、分解生成物により、回収溶剤の品質が
低下する他、ハロゲンイオンは衛生上有害である。特に
塩素イオンは回収装置を激しく腐食するため保守・管理
上も問題となる。従って、吸着・脱着工程における溶剤
の分解性が少ない活性炭が強く要望されていた。
Halogen-based solvents such as chlorofluorocarbon and trichloroethane are easily decomposed, and particularly when they are adsorbed on activated carbon, they are easily decomposed by the catalytic properties of activated carbon and the action of heat or steam added during desorption to generate halogen ions. For this reason, the decomposition products degrade the quality of the recovered solvent, and halogen ions are harmful to sanitation. In particular, chlorine ions corrode the recovery equipment severely, which causes problems in maintenance and management. Accordingly, there has been a strong demand for an activated carbon having a low solvent decomposability in the adsorption / desorption step.

〔問題を解決するための手段〕[Means for solving the problem]

本発明者は有機ハロゲン系溶剤の分解性と粒状活性炭
の表面構造の関係について検討した結果、粒状活性炭の
全酸性基含有率が、有機ハロゲン系溶剤の分解に著しい
影響を及ぼすことを見出し、これについて研究した結果
本発明に到達した。
The present inventor studied the relationship between the decomposability of the organic halogenated solvent and the surface structure of the granular activated carbon, and found that the total acidic group content of the granular activated carbon had a significant effect on the decomposition of the organic halogenated solvent. As a result of research on the present invention, the present invention has been reached.

すなわち、活性炭に含まれる全酸性基量が0.5ミリ当
量/グラム以上、好ましくは1.0ミリ当量/グラム以上
であることを特徴とする、有機ハロゲン系溶剤回収用粒
状活性炭であり、或いは粒状活性炭を酸化することによ
り、全酸性基量を0.5ミリ当量/グラム以上とすること
を特徴とする有機ハロゲン系溶剤回収用活性炭の製法で
ある。
That is, the activated carbon is a granular activated carbon for recovering an organic halogen-based solvent, wherein the total amount of acidic groups contained in the activated carbon is 0.5 meq / g or more, preferably 1.0 meq / g or more. In this method, the total amount of acidic groups is adjusted to 0.5 meq / g or more, thereby producing an activated carbon for recovering an organic halogen-based solvent.

以下、本発明について詳しく説明する。 Hereinafter, the present invention will be described in detail.

ここで、全酸性基量とは、活性炭に希アルカリ溶液を
加えて長時間振とうしたとき、消費されたアルカリの当
量をいう。この値はボエム等の研究(Boem et al:Angew
andte Chemie P.617[1966])によれば、炭素材料の表
面に結合しているカルボニル基、ラクトン基及びカルボ
キシル基の量に該当するとされている。その具体的な定
量法は次の通りである。
Here, the total amount of acidic groups refers to the equivalent amount of alkali consumed when a diluted alkali solution is added to activated carbon and shaken for a long time. This value is based on studies by Boem et al. (Boem et al: Angew
According to andte Chemie P.617 [1966]), it corresponds to the amount of carbonyl group, lactone group and carboxyl group bonded to the surface of the carbon material. The specific quantification method is as follows.

乾燥した粉末活性炭1gを100ml三角フラスコに入れ、
純水50ml及び0.1N NaOH溶液50mlを加えて、振とう器に
て25℃で24時間振とうする。その後、遠心分離器にて80
00rpmで15分試料を沈降させ、その上澄液20mlを100ml三
角フラスコに分取して、全酸性基量を0.1N塩酸による逆
滴定で求める。滴定の際は指示薬としてメチルレッドを
用い、炭酸誤差をなくすため、終点付近で煮沸して炭酸
を追い出し、冷却後再度滴定し、赤みが指したところを
終点とする。(Aml)、同様に空試験を行う(Bml) 全酸性基量Cは C=(B−A)×0.1×f×50/20 C:全酸性基量(meq/g) f:0.1N塩酸のファクター 本発明に使用する粒状活性炭は特に限定しない。オガ
屑、椰子がら等の天然植物、石炭、石油などから得られ
る芳香族多環縮合物、フェノール樹脂などの合成樹脂を
炭化し、常法によって賦活して得られた粒状活性炭であ
る。これらの活性炭の比表面積は特に限定しないが、20
00m2/g以下が好ましい。
Put 1 g of dried powdered activated carbon in a 100 ml Erlenmeyer flask,
Add 50 ml of pure water and 50 ml of 0.1N NaOH solution, and shake with a shaker at 25 ° C. for 24 hours. Then, centrifuge 80
The sample is settled at 00 rpm for 15 minutes, 20 ml of the supernatant is collected in a 100 ml Erlenmeyer flask, and the total amount of acidic groups is determined by back titration with 0.1N hydrochloric acid. At the time of titration, methyl red is used as an indicator, and in order to eliminate carbonic acid error, boiling is driven out near the end point to remove carbonic acid, and after cooling, titration is performed again, and the point indicated by redness is regarded as the end point. (Aml), and perform a blank test in the same manner (Bml) Total acid group amount C: C = (BA) × 0.1 × f × 50/20 C: Total acid group amount (meq / g) f: 0.1N hydrochloric acid Factor of the granular activated carbon used in the present invention is not particularly limited. Granular activated carbon obtained by carbonizing synthetic resins such as aromatic polycyclic condensates obtained from natural plants such as sawdust and coconut palm, coal and petroleum, and phenolic resins, and activating the resin by a conventional method. The specific surface area of these activated carbons is not particularly limited.
00m 2 / g or less is preferable.

粒状活性炭は、破砕状、一定の形状に造粒したもの或
いは顆粒状等の形態で使用することができる。
The granular activated carbon can be used in a crushed form, a granulated form having a predetermined shape, or a granular form.

本発明の活性炭に含まれる全酸性基量は0.5ミリ当量
/グラム以上、好ましくは1.0ミリ当量/グラム以上で
ある必要がある。全酸性基量が0.5ミリ当量/グラム以
下では有機ハロゲン系溶剤の分解性が高く不適当であ
る。また、全酸性基量が多い程溶剤の分解性が低下する
が、特に1.0ミリ当量/グラム以上の領域では分解性が
著しく低下するため、一層好ましい。
The total amount of acidic groups contained in the activated carbon of the present invention must be 0.5 meq / g or more, preferably 1.0 meq / g or more. If the total amount of acidic groups is 0.5 meq / g or less, the organic halogenated solvent is unsuitable because of its high decomposability. Also, the larger the total amount of the acidic groups, the lower the decomposability of the solvent. Particularly, in the region of 1.0 meq / g or more, the decomposability is remarkably reduced, so that it is more preferable.

また、通常の水蒸気或いは炭酸ガスによる賦活法で得
られた活性炭の全酸性基含有量は0.2〜0.4ミリ当量/グ
ラムである。従って、本発明に使用する活性炭を調製す
るためには、全酸性基含有量を大幅に増加させる必要が
ある。
The activated carbon obtained by the ordinary activation method using steam or carbon dioxide has a total acidic group content of 0.2 to 0.4 meq / gram. Therefore, in order to prepare the activated carbon used in the present invention, it is necessary to greatly increase the total acidic group content.

酸性基含有量は活性炭を乾式或いは、湿式酸化により
増加することができる。
The acidic group content can be increased by dry or wet oxidation of activated carbon.

湿式酸化法は、酸化剤として硫酸、過酸化水素、塩
素、硝酸などの水溶液に活性炭を浸漬した後、乾燥し40
0〜500℃で不活性ガス中で熱処理する方法である。
In the wet oxidation method, activated carbon is immersed in an aqueous solution of sulfuric acid, hydrogen peroxide, chlorine, nitric acid, etc. as an oxidizing agent, and then dried and dried.
In this method, heat treatment is performed at 0 to 500 ° C. in an inert gas.

又、乾式酸化法は、空気または、酸素を含むガス中で
200℃以上500℃以下の温度で処理するのが好ましい。20
0℃以下の温度では炭素材料の反応性が低いため、充分
酸化できない。酸化は乾式より湿式のほうが容易で、表
面酸化物の量もコントロールし易く好ましい。酸化処理
は一段階の方式でも良いし、異なる温度で二段階以上に
分けた方式でも良い。酸素を用いる場合は、例えば、1
×10-2torr以上の酸素分圧を有する雰囲気で重量収率が
80%以上になるようにするのが適当である。重量収率を
80%未満にすると表面のエッチングが進行し、重量損失
が大きくなり好ましくない。また、オゾンを含むガスと
低温で接触させてもよいし、或いは、活性炭を酸素プラ
ズマで処理してもよい。例えば、酸素を含むガスを封入
したチューブに活性炭電極を封入して、高圧放電させる
ことにより、本発明の活性炭が得られる。
The dry oxidation method uses air or oxygen-containing gas.
The treatment is preferably performed at a temperature of 200 ° C. or more and 500 ° C. or less. 20
At a temperature of 0 ° C. or less, the carbon material has low reactivity and cannot be sufficiently oxidized. The wet oxidation is easier than the dry oxidation, and the amount of the surface oxide is easily controlled, which is preferable. The oxidation treatment may be a one-step method or a method of dividing the oxidation treatment into two or more steps at different temperatures. When using oxygen, for example, 1
Weight yield in an atmosphere with an oxygen partial pressure of × 10 -2 torr or more
It is appropriate to make it 80% or more. Weight yield
If it is less than 80%, the etching of the surface proceeds and the weight loss increases, which is not preferable. Further, the gas may be brought into contact with a gas containing ozone at a low temperature, or the activated carbon may be treated with oxygen plasma. For example, the activated carbon of the present invention can be obtained by enclosing an activated carbon electrode in a tube in which a gas containing oxygen is enclosed and performing high-pressure discharge.

〔発明の効果〕〔The invention's effect〕

有機ハロゲン系溶剤回収用に本発明の粒状活性炭を使
用すれば、溶剤の吸着・脱着工程における分解性が著し
く低下する。従って、回収された溶剤の品質が向上し、
装置の腐食も大幅に低下して、経済性を著しく改善でき
る。
When the granular activated carbon of the present invention is used for recovering an organic halogen-based solvent, the decomposability in the solvent adsorption / desorption step is significantly reduced. Therefore, the quality of the recovered solvent is improved,
The corrosion of the equipment is also greatly reduced, which can significantly improve the economics.

〔実施例〕〔Example〕

以下実施例によって、本発明を具体的に説明するが、
本発明はこれによって何ら限定されるものではない。
Hereinafter, the present invention will be described specifically with reference to Examples.
The present invention is not limited by this.

実施例1、2比較例1 100〜300メッシュに粉砕した椰子がら炭100部、コー
ルタールピッチ30部、重油4部、水15部をよく混合して
3mmのペレットに造粒し、ロータリーキルンで小量の空
気を吹き込みながら250℃に加熱して酸化し、さらに空
気の吹き込みを停止した後、650℃まで昇温して乾留し
た。次に流動賦活炉に液化石油ガスを燃焼せしめたガス
と水蒸気を吹き込み、850℃で4時間賦活した後、塩酸
洗浄、水洗、乾燥して、全酸性基量は0.21meq/gの活性
炭(比較例1)を得た。
Examples 1 and 2 Comparative Example 1 100 parts of coconut charcoal pulverized to 100 to 300 mesh, 30 parts of coal tar pitch, 4 parts of heavy oil, and 15 parts of water were mixed well.
The mixture was granulated into pellets of 3 mm, oxidized by heating to 250 ° C. while blowing a small amount of air with a rotary kiln, and further stopping the blowing of air, followed by heating to 650 ° C. and dry distillation. Next, the gas and steam which burned liquefied petroleum gas were blown into the fluidized activation furnace, activated at 850 ° C for 4 hours, washed with hydrochloric acid, washed with water and dried, and activated carbon with a total acid group content of 0.21meq / g (compared to Example 1) was obtained.

これを500℃の空気中で1時間酸化し、収率94%で全
酸性基量0.84meq/gの活性炭を得た(実施例1)。さら
に条件を変えて全酸性基量1.63meq/gの活性炭(実施例
2)を得た。
This was oxidized in air at 500 ° C. for 1 hour to obtain activated carbon having a yield of 94% and a total acidic group content of 0.84 meq / g (Example 1). Activated carbon (Example 2) having a total acidic group content of 1.63 meq / g was obtained by further changing the conditions.

これらの活性炭により、フロン113の分解率を測定し
た。
The decomposition rate of Freon 113 was measured using these activated carbons.

溶剤の分解率は、内径18mmのガラスカラムに試料45ml
を充填し、200℃に加熱し、これにフロン及び純水を60m
l/hrで1時間供給し、流出ガスをアルカリ溶液でトラッ
プし、溶液中の塩素イオンをチオシアン酸アンモニウム
滴定法で定量した。活性炭中の塩素はアルカリ溶液で煮
沸し、溶液中の塩素イオンを同様に定量した。流出液及
び活性炭中の塩素量から分解率を計算した。同様に1,1,
1−トリクロロエタンの150℃における分解率を測定し
た。その結果を第1表に示す。
The decomposition rate of the solvent is as follows.
And heated to 200 ° C.
The solution was supplied at 1 / hr for 1 hour, the effluent gas was trapped with an alkaline solution, and the chloride ion in the solution was quantified by ammonium thiocyanate titration. Chlorine in activated carbon was boiled with an alkaline solution, and chloride ions in the solution were similarly quantified. The decomposition rate was calculated from the amount of chlorine in the effluent and activated carbon. Similarly 1,1,
The decomposition rate of 1-trichloroethane at 150 ° C. was measured. Table 1 shows the results.

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) C01B 31/08 B01J 20/20 B01D 53/70 B01D 53/02 ──────────────────────────────────────────────────続 き Continued on the front page (58) Field surveyed (Int. Cl. 7 , DB name) C01B 31/08 B01J 20/20 B01D 53/70 B01D 53/02

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】粒状活性炭に含まれる全酸性基量が0.5ミ
リ当量/グラム以上であることを特徴とする、有機ハロ
ゲン系溶剤回収用粒状活性炭。
1. A granular activated carbon for recovering an organic halogen-based solvent, wherein the total amount of acidic groups contained in the granular activated carbon is 0.5 meq / g or more.
【請求項2】粒状活性炭の全酸性基量が1.0ミリ当量/
グラム以上である特許請求の範囲、第1項記載の有機ハ
ロゲン系溶剤回収用粒状活性炭。
2. The granular activated carbon has a total acidic group content of 1.0 meq / g.
The granular activated carbon for recovering an organic halogen-based solvent according to claim 1, which is not less than gram.
【請求項3】粒状活性炭を酸化せしめることにより、全
酸性基量が0.5ミリ当量/グラム以上とすることを特徴
とする、有機ハロゲン系溶剤回収用粒状活性炭の製法。
3. A method for producing a granular activated carbon for recovering an organic halogen-based solvent, wherein the total amount of acidic groups is adjusted to 0.5 meq / g or more by oxidizing the granular activated carbon.
JP2158401A 1990-06-15 1990-06-15 Activated carbon for recovery of organic halogenated solvents Expired - Fee Related JP3027763B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2158401A JP3027763B2 (en) 1990-06-15 1990-06-15 Activated carbon for recovery of organic halogenated solvents

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2158401A JP3027763B2 (en) 1990-06-15 1990-06-15 Activated carbon for recovery of organic halogenated solvents

Publications (2)

Publication Number Publication Date
JPH0450110A JPH0450110A (en) 1992-02-19
JP3027763B2 true JP3027763B2 (en) 2000-04-04

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ID=15670941

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Country Link
JP (1) JP3027763B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002338222A (en) * 2001-05-10 2002-11-27 Futamura Chemical Industries Co Ltd Method for preparing activated carbon having controlled quantity of surface oxide
CN103172064A (en) * 2013-04-12 2013-06-26 宁夏大学 Low-ash coal-based activated carbon quick activation production technology
WO2016067440A1 (en) * 2014-10-31 2016-05-06 大阪ガスケミカル株式会社 Fibrous activated carbon for solvent recovery

Also Published As

Publication number Publication date
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