JP3430385B2 - Cleaning method of membrane - Google Patents

Cleaning method of membrane

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Publication number
JP3430385B2
JP3430385B2 JP25973195A JP25973195A JP3430385B2 JP 3430385 B2 JP3430385 B2 JP 3430385B2 JP 25973195 A JP25973195 A JP 25973195A JP 25973195 A JP25973195 A JP 25973195A JP 3430385 B2 JP3430385 B2 JP 3430385B2
Authority
JP
Japan
Prior art keywords
membrane
filtration tank
cleaning
water
raw water
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
JP25973195A
Other languages
Japanese (ja)
Other versions
JPH0999226A (en
Inventor
義公 渡邊
源三 小澤
辰彦 鈴木
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Maezawa Industries Inc
Original Assignee
Maezawa Industries Inc
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 Maezawa Industries Inc filed Critical Maezawa Industries Inc
Priority to JP25973195A priority Critical patent/JP3430385B2/en
Publication of JPH0999226A publication Critical patent/JPH0999226A/en
Application granted granted Critical
Publication of JP3430385B2 publication Critical patent/JP3430385B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Separation Using Semi-Permeable Membranes (AREA)

Description

【発明の詳細な説明】 【0001】 【発明の属する技術分野】この発明は、濾過槽内に導入
した原水を膜モジュールに透過させ、固液分離を継続す
ることにより、付着物で閉塞された膜を効率よく洗浄す
る膜の洗浄方法に関するものである。 【0002】 【従来の技術】水処理設備においては、原水を濾過膜に
流して透過させ、固液分離を行っている。この膜濾過装
置は、濾過槽内に膜モジュールを浸漬してあり、濾過槽
内に導入した原水を膜モジュールの中空糸膜により濾過
する。透過水は、吸引ポンプにより送水され、浄水用の
処理水として供される。 【0003】上記の膜濾過装置において、膜濾過を継続
すると、濁質等の付着物により膜に目詰まりが生じ濾過
効率が低下するので、一定時間使用すると、透過水を膜
の透過水側から原水側に逆流させる逆洗浄といわれる方
法で膜を洗浄したり、濾過槽内の膜の下方に設けた空気
ノズルからの気泡により膜の表面を洗浄するようにして
いる。 【0004】さらに、一定期間経過すると、濁質等の付
着物は膜層の内部にまで入り込み、上記の方法による洗
浄効果が著しく低下するので、このような事態に至った
ときは、従来、膜を装置から取り外して、洗浄用の薬液
(酸・アルカリ)が貯留された薬液洗浄槽内に浸漬させ
て膜の洗浄を行っている。また、膜を装置から取り外さ
ず、膜に洗浄用の薬液を供給して、この薬液により膜の
付着物を除去しようとする試みもなされている。 【0005】 【発明が解決しようとする課題】しかしながら、上記の
従来の夫々の方法では、膜を閉塞する付着物の完全な除
去は難しい。中でも、付着物が有機物,金属等である場
合はともかく、これが微生物である場合には、その除去
作業がより困難となる。すなわち、特に浸漬型膜濾過装
置のように装置内の水の入れ替わりが比較的少ない系で
は、微生物が膜の表面に強固に付着しているので、膜の
フラックスが大きく低下し、従来の洗浄方法ではその除
去は到底不可能である。そして、従来の膜を濾過装置か
ら取り外して薬液洗浄槽内に浸漬させる方法では、クレ
ーン等、膜の移動および取り外し・取り付けのための設
備が必要となる。また、膜を装置から取り外さず膜に洗
浄用の薬液を供給させる方法では、薬液洗浄後の廃液処
理に手間がかかる欠点がある。 【0006】この発明は、このような従来の薬液による
膜の洗浄方法に代え、濾過槽内を嫌気状態として膜から
付着物を剥離する方法を採用することにより、膜のフラ
ックスを回復する膜の洗浄方法を提供することを目的と
する。 【0007】 【課題を解決するための手段】上記の目的を達成するた
めの具体的手段として、この発明は、濾過槽内に導入し
た原水を膜モジュールに透過させ、固液分離を継続する
ことにより、付着物で閉塞された膜を洗浄するに当り、
濾過槽内を所定時間嫌気状態に維持する間に、膜を閉塞
している付着微生物を変質させて剥離し、分離除去する
とともに、酸化還元電位を低下させることにより、溶解
性金属を除去することを特徴とする膜の洗浄方法を構成
した。 【0008】この場合、濾過槽内を嫌気状態とする方法
としては、濾過槽内に還元剤(特に亜硫酸ナトリウム、
亜硫酸水素ナトリウム)を投入する方法、あるいは、濾
過槽内の原水中の酸素を窒素ガスで置換する方法が有効
である。また、嫌気状態を維持した後膜から付着物を剥
離するには、濾過槽内に、ブロワから送られた空気を吹
き込む方法が有効である。さらに、膜モジュールは、浸
漬型濾過膜とするとよい。 【0009】 【発明の実施の形態】以下に、この発明の実施の形態を
図面に基づき説明する。図1の(a)は、この発明に係
る膜の洗浄方法を説明するための浸漬型膜濾過装置の一
例を示す断面図であり、同図の(b)は、膜モジュール
の斜視図である。 【0010】図1の(a)および(b)を参照して、下
部を円錐状とした略円筒形の濾過槽1内には原水2が公
知の手段により導入される。原水2中には、浸漬型濾過
膜である膜モジュール3が横配置で上下に2基吊設され
ている。膜モジュール3は、中空糸膜3a(以下、膜3
aという。)を多数集積したもので、個々の膜3aは両
端部を夫々連結するとともに、両端部で内側内を連通し
てある。原水2は、吸引ポンプ10に吸引されて膜モジ
ュール3の膜3aの外側から膜3aの内側に透過し濾過
される。透過水11は、膜モジュール3の両側の配管1
8,19を繋いだ送水管13を経由して濾過槽1の外部
に取り出され、吸引ポンプ10により処理水槽17へ送
られ、浄水用の処理水12として供される。15は、送
水管13上における吸引ポンプ10の濾過槽1側に介装
された開閉弁であり、送水中は開状態となっている。 【0011】処理水槽10と送水管13との間には逆洗
浄用の配管20が接続され、逆洗ポンプ21と開閉弁1
6が介設される。膜モジュール3の膜3aに付着物が付
着し目詰まりが生じたときは、吸引ポンプ10を停止
し、開閉弁15を閉じ、開閉弁16を開状態として逆洗
ポンプ21を作動させて、膜3aの内側から圧縮された
空気および水を送り込み、逆洗浄を行う。なお、濾過槽
1の底部には、膜3aにより分離された付着物の集合体
である汚泥22が沈滞している。 【0012】さて、膜濾過を継続しつつ、さらに、一定
期間経過することにより、膜3aに付着物、特に微生物
が堆積して膜3aが閉塞されると、原水2の供給を停止
し、また、吸引ポンプ10および逆洗ポンプ21を作動
停止した後、開閉弁15,16を閉じ、膜の洗浄が行わ
れる。その第1の手段としては、濾過槽1内に貯留され
た原水2中に還元剤5を投入し、濾過槽1内を嫌気状態
とする方法が挙げられる。還元剤には、例えば水溶性の
亜硫酸ナトリウムや亜硫酸水素ナトリウムその他の毒性
のない公知の化合物が選定される。第2の手段として
は、窒素ガスの散気で、濾過槽1内を嫌気状態とする方
法が挙げられる。すなわち、濾過槽1内に貯留された原
水2中に多孔管6を配置し、窒素ガスを貯蔵したボンベ
7から原水2中に窒素ガスを送り込み、原水2中の酸素
を窒素ガスで置換するものである。この嫌気状態を所定
時間、具体的には約1日以上維持することにより、付着
微生物は変質して膜表面から剥離され、分離除去され
る。なお、嫌気状態でさらに酸化還元電位を低下させる
と、金属類の多くが還元状態で溶解性となることより、
金属等の詰まりに関しても有効に除去できる。また、濾
過槽1内を所定時間嫌気状態に維持した後、膜を振動さ
せて膜から付着物を剥離させてもよい。さらに、振動に
代えて逆洗浄を行ってもよい。次いで、濾過槽1内に
は、ブロワ9から空気が送られ、これを原水2中に配置
した多孔管8で細かい気泡にして均一に原水2中に吹き
込む散気装置により、付着微生物を膜から剥離させた
後、運転が再開される。この場合、散気装置からの空気
は、膜の表面に当るようにするとよい。濾過槽1内の水
は、必要に応じてドレンする。 【0013】なお、上記の実施形態においては、原水中
に膜モジュールを2基吊設した例について説明したが、
規模に応じて増減される。また、膜モジュールは中空糸
膜に代えて平膜やスパイラル膜あるいは管状膜等を使用
してもよい。 【0014】 【発明の効果】以上説明したように、この発明に係る膜
の洗浄方法によれば、濾過槽内を嫌気化して膜から付着
物を剥離する方法を採用したので、膜の表面に強固に付
着し膜を閉塞している付着物、特に微生物が、濾過槽内
の嫌気状態を維持している間に変質して剥離し、膜のフ
ラックスを大きく回復し得た。したがって、従来の洗浄
方法では困難であった付着物の完全除去が可能である。
そして、従来の膜を濾過装置から取り外して薬液洗浄槽
内に浸漬させる方法が必要とした、クレーン等、膜の移
動および取り外し・取り付けのための設備が不要とな
る。また、従来の膜を装置から取り外さず膜に洗浄用の
薬液を供給させる方法が必要とした薬液洗浄後の廃液処
理は、窒素ガスの散気による場合は不要であり、還元剤
を投入する場合も少量の廃液で済む効果がある。
Description: BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention permeates raw water introduced into a filtration tank through a membrane module and continues solid-liquid separation, whereby the raw water is blocked by deposits. The present invention relates to a method for cleaning a film for efficiently cleaning the film. 2. Description of the Related Art In a water treatment facility, raw water flows through a filtration membrane and is permeated to perform solid-liquid separation. In this membrane filtration device, a membrane module is immersed in a filtration tank, and raw water introduced into the filtration tank is filtered by a hollow fiber membrane of the membrane module. The permeated water is sent by a suction pump and provided as treated water for water purification. In the above-mentioned membrane filtration apparatus, if the membrane filtration is continued, the membrane is clogged by a deposit such as turbidity and the filtration efficiency is reduced. The membrane is washed by a method called back washing, in which the membrane flows back to the raw water side, or the surface of the membrane is washed by air bubbles from an air nozzle provided below the membrane in the filtration tank. Further, after a certain period of time, deposits such as turbid substances enter into the inside of the membrane layer, and the cleaning effect by the above-mentioned method is remarkably deteriorated. Is removed from the apparatus, and immersed in a chemical cleaning tank in which a cleaning chemical (acid / alkali) is stored to clean the membrane. Also, attempts have been made to supply a chemical solution for cleaning to the film without removing the film from the apparatus, and to remove deposits on the film with the chemical solution. [0005] However, it is difficult to completely remove the deposits blocking the film by each of the above-mentioned conventional methods. Above all, if the attached matter is an organic matter, a metal or the like, and if the attached matter is a microorganism, the removing operation becomes more difficult. That is, especially in a system such as an immersion type membrane filtration device in which the water exchange in the device is relatively small, since the microorganisms are strongly attached to the surface of the membrane, the flux of the membrane is greatly reduced, and the conventional cleaning method is used. Then it is impossible to remove it. In the conventional method of removing the membrane from the filtering device and immersing the membrane in the chemical solution cleaning tank, equipment such as a crane for moving, removing, and attaching the membrane is required. Further, the method of supplying a chemical solution for cleaning to the film without removing the film from the apparatus has a disadvantage that it takes time and effort to treat a waste liquid after the chemical solution cleaning. The present invention employs a method in which the inside of a filtration tank is made anaerobic to remove deposits from the membrane, instead of the conventional method of cleaning a membrane with a chemical solution, thereby recovering the flux of the membrane. It is intended to provide a cleaning method. [0007] As a specific means for achieving the above object, the present invention is to permeate raw water introduced into a filtration tank through a membrane module and continue solid-liquid separation. As a result, in cleaning the membrane clogged with the deposit,
The membrane is blocked while maintaining the anaerobic state in the filtration tank for a predetermined time
Transforms and separates and removes attached microorganisms.
And by lowering the oxidation-reduction potential,
A method for cleaning a film, comprising removing a reactive metal . In this case, as a method for making the inside of the filtration tank anaerobic, a reducing agent (particularly sodium sulfite,
A method of introducing sodium hydrogen sulfite) or a method of replacing oxygen in raw water in a filtration tank with nitrogen gas is effective. Further, in order to separate the deposits from the membrane after maintaining the anaerobic state, it is effective to blow air sent from a blower into the filtration tank. Further, the membrane module may be an immersion filtration membrane. Embodiments of the present invention will be described below with reference to the drawings. FIG. 1A is a cross-sectional view showing an example of a submerged membrane filtration device for explaining a membrane cleaning method according to the present invention, and FIG. 1B is a perspective view of a membrane module. . Referring to FIGS. 1 (a) and 1 (b), raw water 2 is introduced into a generally cylindrical filtration tank 1 having a conical lower portion by known means. In the raw water 2, two membrane modules 3, which are immersion-type filtration membranes, are vertically suspended in a horizontal arrangement. The membrane module 3 includes a hollow fiber membrane 3a (hereinafter, membrane 3).
called a. ) Are integrated, and the individual films 3a are connected at both ends thereof and communicate with the inside at both ends. The raw water 2 is sucked by the suction pump 10 and permeates from the outside of the membrane 3a of the membrane module 3 to the inside of the membrane 3a to be filtered. The permeated water 11 is supplied to the piping 1 on both sides of the membrane module 3.
The water is taken out of the filtration tank 1 through a water supply pipe 13 connecting the pipes 8 and 19, sent to a treatment water tank 17 by a suction pump 10, and provided as treatment water 12 for water purification. Reference numeral 15 denotes an opening / closing valve interposed on the filtration tank 1 side of the suction pump 10 on the water supply pipe 13, and is open during water supply. A backwashing pipe 20 is connected between the treated water tank 10 and the water pipe 13, and a backwash pump 21 and an on-off valve 1 are provided.
6 are interposed. When deposits adhere to the membrane 3a of the membrane module 3 and clogging occurs, the suction pump 10 is stopped, the on-off valve 15 is closed, the on-off valve 16 is opened, and the backwash pump 21 is operated to operate the membrane. Compressed air and water are sent from the inside of 3a to perform back washing. At the bottom of the filtration tank 1, sludge 22, which is an aggregate of attached matter separated by the membrane 3a, is stagnating. [0012] When a certain period of time elapses while the membrane filtration is continued and the deposits, especially microorganisms, accumulate on the membrane 3a and the membrane 3a is closed, the supply of the raw water 2 is stopped. After the operation of the suction pump 10 and the backwash pump 21 is stopped, the on-off valves 15 and 16 are closed, and the membrane is washed. As the first means, there is a method in which the reducing agent 5 is charged into the raw water 2 stored in the filtration tank 1 to make the inside of the filtration tank 1 an anaerobic state. As the reducing agent, for example, water-soluble sodium sulfite, sodium hydrogen sulfite and other known non-toxic compounds are selected. As a second means, there is a method in which the inside of the filtration tank 1 is made anaerobic by diffusing nitrogen gas. That is, a perforated pipe 6 is arranged in raw water 2 stored in a filtration tank 1, nitrogen gas is sent into the raw water 2 from a cylinder 7 storing nitrogen gas, and oxygen in the raw water 2 is replaced with nitrogen gas. It is. By maintaining this anaerobic state for a predetermined period of time, specifically, about one day or more, the attached microorganisms are degenerated and separated from the membrane surface, and separated and removed. If the oxidation-reduction potential is further reduced in the anaerobic state, most of the metals become soluble in the reduced state,
The clogging of metal or the like can be effectively removed. Alternatively, after maintaining the inside of the filtration tank 1 in an anaerobic state for a predetermined time, the film may be vibrated to separate the deposit from the film. Further, back washing may be performed instead of vibration. Next, air is sent from the blower 9 into the filtration tank 1, and the adhered microorganisms are removed from the membrane by a diffuser that uniformly blasts the raw water 2 into fine bubbles with a porous tube 8 arranged in the raw water 2. After peeling, the operation is resumed. In this case, the air from the air diffuser should preferably hit the surface of the membrane. The water in the filtration tank 1 is drained as needed. In the above embodiment, an example in which two membrane modules are suspended in raw water has been described.
It is increased or decreased according to the scale. Further, the membrane module may use a flat membrane, a spiral membrane, a tubular membrane, or the like instead of the hollow fiber membrane. As described above, according to the method for cleaning a membrane according to the present invention, the method of anaerobicizing the inside of the filtration tank and removing the deposits from the membrane is adopted. Deposits, especially microorganisms, which adhered tightly and blocked the membrane, were altered and peeled off while maintaining the anaerobic state in the filtration tank, and the flux of the membrane could be largely recovered. Therefore, it is possible to completely remove the deposits, which is difficult with the conventional cleaning method.
In addition, equipment for moving, removing, and attaching the membrane, such as a crane, which required the conventional method of removing the membrane from the filtration device and immersing it in the chemical solution cleaning tank, is not required. In addition, the conventional method of supplying a chemical solution for cleaning to a membrane without removing the membrane from the apparatus is necessary, and the waste liquid treatment after chemical solution washing is unnecessary when diffusing nitrogen gas, and when a reducing agent is supplied. This also has the effect of requiring only a small amount of waste liquid.

【図面の簡単な説明】 【図1】(a)は、この発明に係る膜の洗浄方法を説明
するための浸漬型膜濾過装置の一例を示す断面図であ
り、(b)は、膜モジュールの斜視図である。 【符号の説明】 1 …濾過槽 2 …原水 3 …膜モジュール 3a…中空糸膜 5 …還元剤 6 …多孔管 7 …ボンベ 8 …多孔管 9 …ブロワ 10 …吸引ポンプ 11 …透過水 12 …処理水 13 …送水管 15 …開閉弁 16 …開閉弁 17 …処理水槽 18 …配管 19 …配管 20 …配管 21 …逆洗ポンプ 22 …汚泥
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 (a) is a cross-sectional view showing an example of a submerged membrane filtration device for explaining a membrane cleaning method according to the present invention, and FIG. 1 (b) is a membrane module. It is a perspective view of. [Description of Signs] 1 ... filtration tank 2 ... raw water 3 ... membrane module 3a ... hollow fiber membrane 5 ... reducing agent 6 ... porous tube 7 ... cylinder 8 ... porous tube 9 ... blower 10 ... suction pump 11 ... permeated water 12 ... treatment Water 13 ... Water supply pipe 15 ... On-off valve 16 ... On-off valve 17 ... Treatment water tank 18 ... Pipe 19 ... Pipe 20 ... Pipe 21 ... Backwash pump 22 ... Sludge

フロントページの続き (72)発明者 鈴木 辰彦 東京都中央区京橋1丁目3番3号前澤工 業株式会社内 (56)参考文献 特開 平7−155789(JP,A) 特開 昭55−129107(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01D 65/02 520 B01D 65/06 C02F 1/44 Continuation of the front page (72) Inventor Tatsuhiko Suzuki 1-3-3 Kyobashi, Chuo-ku, Tokyo Inside Maezawa Industrial Co., Ltd. (56) References JP-A-7-155789 (JP, A) JP-A-55-129107 (JP, A) (58) Field surveyed (Int. Cl. 7 , DB name) B01D 65/02 520 B01D 65/06 C02F 1/44

Claims (1)

(57)【特許請求の範囲】 【請求項1】 濾過槽内に導入した原水を膜モジュール
に透過させ、固液分離を継続することにより、付着物で
閉塞された膜を洗浄するに当り、濾過槽内を所定時間嫌
気状態に維持する間に、膜を閉塞している付着微生物を
変質させて剥離し、分離除去するとともに、酸化還元電
位を低下させることにより、溶解性金属を除去すること
を特徴とする膜の洗浄方法。
(57) [Claims 1] In washing the membrane clogged with deposits, the raw water introduced into the filtration tank is allowed to permeate through the membrane module and solid-liquid separation is continued. While maintaining the inside of the filtration tank in an anaerobic state for a predetermined time , attached microorganisms blocking the membrane are removed.
Degradation and peeling, separation and removal, and oxidation-reduction
A method for cleaning a film, comprising: removing a soluble metal by lowering a position .
JP25973195A 1995-10-06 1995-10-06 Cleaning method of membrane Expired - Fee Related JP3430385B2 (en)

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Application Number Priority Date Filing Date Title
JP25973195A JP3430385B2 (en) 1995-10-06 1995-10-06 Cleaning method of membrane

Publications (2)

Publication Number Publication Date
JPH0999226A JPH0999226A (en) 1997-04-15
JP3430385B2 true JP3430385B2 (en) 2003-07-28

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JP2005074357A (en) * 2003-09-02 2005-03-24 Ngk Insulators Ltd Membrane washing method in membrane separation activated sludge method
JP5290801B2 (en) * 2009-02-17 2013-09-18 株式会社アクト Sewage treatment apparatus and sewage treatment method
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