JP4031345B2 - Method for drying hydrous waste - Google Patents
Method for drying hydrous waste Download PDFInfo
- Publication number
- JP4031345B2 JP4031345B2 JP2002305408A JP2002305408A JP4031345B2 JP 4031345 B2 JP4031345 B2 JP 4031345B2 JP 2002305408 A JP2002305408 A JP 2002305408A JP 2002305408 A JP2002305408 A JP 2002305408A JP 4031345 B2 JP4031345 B2 JP 4031345B2
- Authority
- JP
- Japan
- Prior art keywords
- waste
- water
- drying
- hydrous
- dried
- 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 - Lifetime
Links
Images
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
Landscapes
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
- Drying Of Solid Materials (AREA)
Description
【0001】
【発明の属する技術分野】
本発明は各種含水廃棄物から効果的に水分を乾燥させる方法に関する。
【0002】
【従来の技術】
食品残渣、農産物廃棄物、魚・肉畜産残渣や汚泥等の含水廃棄物を飼料や肥料等として再利用するため、あるいは減容して廃棄するために、これらを加熱し、水分を蒸発させて乾燥させることが従来から行われている。
乾燥には、悪臭の発生を防止し、除去水分の処理を容易にするために、減圧乾燥機(真空乾燥機)が使用される場合が多くなりつつある。
【0003】
【発明が解決しようとする課題】
減圧乾燥は、熱効率を高めるために、通常、被乾燥物を攪拌しながら行われるが、被乾燥物の内部に含まれる水分の蒸散に時間が掛かり、乾燥時間が長くなり、熱効率を悪化させていた。特に、被乾燥物が農・畜産廃棄物や活性汚泥等の場合には、動・植物細胞や微生物細胞中に含まれる水分が、細胞膜を通過するのに長時間を要し、乾燥操作の障害になっていた。
従って、本発明の目的は、含水廃棄物中に動・植物や活性汚泥の微生物のような内部水を有するものが含まれている場合にも、効率的な乾燥ができる方法を提供することである。
【0004】
被乾燥物の固形分周辺にある外部水と動・植物あるいは微生物等の内部に含まれる内部水では、外部水の蒸発速度の方が格段に速い。
この理由は、(1)外部水は固形物の外側にあるため、乾燥用熱風あるいは伝熱面との接触効率がよいこと、(2)内部水は細胞膜で囲まれており、細胞膜が内部水の拡散を阻害するためである。
【0005】
本発明者は、内部水の乾燥を促進すべく種々検討した結果、被乾燥物を無機塩又は無機酸の存在下に乾燥させると、先ず被乾燥物に付着した外部水が蒸発するが、外部水の蒸発に伴い、無機塩又は無機酸の濃度が上昇して外部水の浸透圧が高くなり、植物や微生物の内部水が外部水側に移行することにより、内部水の蒸発速度が上昇することを見いだし、本発明を完成するに至った。
【0006】
【課題を解決するための手段】
上記目的は、以下の本発明によって達成される。即ち、本発明は、動・植物又は微生物が含まれている含水廃棄物を、無機塩又は無機酸の存在下に真空乾燥機を用いて乾燥させる含水廃棄物の乾燥方法であって、上記無機塩が、Na2SO4、NaNO3、NaH2PO4、Na2HPO4、Na3PO4、CaCl2、Ca(NO3)2及びMgCl2から選ばれるいずれかであり、無機酸がりん酸であり、且つ、無機塩又は無機酸を、含水廃棄物中の含有水分に対して0.01〜10重量%の範囲で存在させることを特徴とする含水廃棄物の乾燥方法である。
【0007】
【発明の実施の形態】
以下に、好ましい実施の形態を挙げて、本発明をさらに詳細に説明する。
本発明が対象とする含水廃棄物としては、例えば、おから、酒粕、お茶やコーヒー等の使用滓、家庭及び飲食店等からの生ごみ等の食品残渣;魚肉・畜産廃棄物;野菜くず、野菜・果物搾り滓等の農産廃棄物;活性汚泥等の各種汚泥;加圧浮上スカム;牛・豚・鶏等の家畜の糞尿;各種濃厚廃液等が挙げられる。含水廃棄物の種類は特に限定されず、又、含水率も限定されない。
本発明は動・植物の残渣や微生物を含む汚泥等の内部水を有する物体を含む含水廃棄物の乾燥に好適である。
【0008】
本発明の特徴は、上記のような含水廃棄物を乾燥して水分を除去する際に、無機塩又は無機酸(鉱酸)を共存させることである。
本発明で使用する無機塩は、無機酸(鉱酸)のアルカリ金属又はアルカリ土類金属の塩が好ましく、例えば、Na2SO4、NaNO3、NaH2PO4、Na2HPO4、Na3PO4、CaCl2、Ca(NO3)2、MgCl2等が挙げられる。無機酸(鉱酸)としては、りん酸が挙げられる。無機塩又は無機酸は、乾燥された含水廃棄物の再利用を考慮して選択することが望ましい。
【0009】
含水廃棄物を乾燥する際には、含水廃棄物の形態(含水固形物、固形物のスラリー、液体等)に応じた乾燥機が使用される。例えば、通気箱形乾燥機、通気バンド乾燥機、回転乾燥機(通常真空式で、円筒状乾燥機自体が回転する。加熱方式に、直接加熱式と間接加熱式とがある。)、噴霧乾燥機(スプレードライヤー)、蒸発缶、回転しない円筒状乾燥機内に設けた攪拌羽根の回転によって被乾燥物を攪拌して乾燥を促進する(間接加熱方式の場合は乾燥機壁面と、直接加熱方式では加熱媒体(通常は水蒸気又は加熱空気等)との、絶えず更新される被乾燥物との接触により)とともに、乾燥した被乾燥物を粉砕する撹拌型真空乾燥機等が挙げられる。本発明における好ましい乾燥機は、密閉式で悪臭が外部へ漏れず、悪臭の吸着等による除去や水分の回収及び処理が容易な上記の撹拌型真空乾燥機である。真空乾燥機を使用し、真空度を調製することで、例えば、50℃程度の低温での含水廃棄物の乾燥が可能である。真空乾燥機の運転条件は、特に限定されず、含水廃棄物の含水率に応じて適宜設定することができる。
【0010】
含水廃棄物を真空乾燥する際、含水廃棄物の含水率に応じて無機塩又は無機酸の使用量を調整する。通常、無機塩又は無機酸は含水廃棄物の含有水分に対して0.001〜10重量%となる量で使用することが好ましく、更に好ましくは0.01〜10重量%である。含水廃棄物中に動・植物や微生物が含まれていたり、あるいは内部に水分を吸収している固形物が含まれている場合には上記の量を更に10〜50重量%程度増量することが好ましい。
含水廃棄物への無機塩又は無機酸の添加は、予めそれらを含水廃棄物に混合及び溶解してから真空乾燥機に投入しても、あるいは含水廃棄物を真空乾燥機に投入してから無機塩又は無機酸を添加、溶解させてもよい。
【0011】
真空乾燥機を使用することにより、回収された水分は、そのまま、あるいは必要により処理して再利用したり、河川に放水することができる。一方、乾燥した粉末状の廃棄物は、その種類によっては、飼料や肥料として再利用することができる。
【0012】
【実施例】
以下に実施例及び比較例を挙げて本発明を具体的に説明する。
【0013】
実施例1、比較例1
図1に概略断面図を示す撹拌型円筒状真空乾燥機(実容積0.33m3、伝熱面積4.99m2、撹拌動力2.2kw)を用いて下記の含水廃棄物の乾燥を行なった。
含水率83重量%の活性汚泥ケーキ200kgを真空乾燥機に投入し、次いで塩化カルシウム(CaCl2)を0.5kg(水分に対して0.3重量%)投入して乾燥を開始した。真空度75mmHg(10kPa)、内温55℃の条件で6時間乾燥させた。乾燥した廃棄物は粉末状で、含水率は4.8重量%であった。
又、塩化カルシウムを使用しない以外は上記と同じ含水廃棄物を同じ条件で乾燥させた。乾燥廃棄物の含水率は28重量%で、粉末化も不充分であった。上記と同じ含水率となるまでの全乾燥時間は11時間であった。
【0014】
実施例2、比較例2
実施例1と同じ真空乾燥機を用い、含水率96重量%の野菜くず120kgを投入し、次いで、りん酸0.3kg(水分に対して0.27重量%)投入して実施例1及び比較例1と同じ条件で6時間乾燥させた。本発明方法による乾燥廃棄物は、粉末状で、含水率は8.2重量%であった。一方、比較例の乾燥廃棄物は含水率が33重量%であり、上記と同じ含水率となるまでの全乾燥時間は13時間であった。
【0015】
【発明の効果】
以上の本発明によれば、含水廃棄物中に内部水を有する植物や微生物等が含まれている場合にも、効率的に乾燥でき、乾燥廃棄物のリサイクルも可能な、含水廃棄物の乾燥方法が提供される。
【図面の簡単な説明】
【図1】 本発明で使用する撹拌型真空乾燥機の一例の概略断面図である。[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for effectively drying moisture from various hydrous wastes.
[0002]
[Prior art]
In order to reuse food waste, agricultural waste, fish / meat livestock residue, sludge and other water-containing waste as feed, fertilizer, etc. Drying is conventionally performed.
In drying, in order to prevent the generation of malodor and facilitate the treatment of the removed moisture, a vacuum dryer (vacuum dryer) is increasingly used.
[0003]
[Problems to be solved by the invention]
In order to increase the thermal efficiency, vacuum drying is usually performed while stirring the material to be dried, but it takes time to evaporate the water contained in the material to be dried, which increases the drying time and deteriorates the thermal efficiency. It was. In particular, if the material to be dried is agricultural / livestock waste, activated sludge, etc., it takes a long time for moisture contained in animal / plant cells and microbial cells to pass through the cell membrane, impairing the drying operation. It was.
Therefore, an object of the present invention is to provide a method capable of efficient drying even when the water-containing waste contains internal water such as microorganisms of animals, plants and activated sludge. is there.
[0004]
The evaporation rate of the external water is much faster in the external water around the solid content of the material to be dried and in the internal water contained in animals / plants or microorganisms.
This is because (1) the external water is outside the solid, so that the contact efficiency with the hot air for drying or the heat transfer surface is good. (2) The internal water is surrounded by the cell membrane, and the cell membrane is internal water. This is to inhibit the diffusion of.
[0005]
As a result of various studies to promote the drying of internal water, the present inventor first dried the object to be dried in the presence of an inorganic salt or an inorganic acid. As the water evaporates, the concentration of inorganic salt or acid increases and the osmotic pressure of the external water increases, and the internal water of plants and microorganisms moves to the external water side, thereby increasing the evaporation rate of the internal water. As a result, the present invention has been completed.
[0006]
[Means for Solving the Problems]
The above object is achieved by the present invention described below. That is, the present invention is a method for drying hydrous waste, which comprises drying hydrous waste containing animals, plants, or microorganisms using a vacuum dryer in the presence of an inorganic salt or an inorganic acid. The salt is any one selected from Na 2 SO 4 , NaNO 3 , NaH 2 PO 4 , Na 2 HPO 4 , Na 3 PO 4 , CaCl 2 , Ca (NO 3 ) 2 and MgCl 2 , and the inorganic acid is phosphorus Sandea is, and, an inorganic salt or an inorganic acid, is a method for drying water-containing waste, characterized in Rukoto is present in the range of 0.01 to 10% by weight relative to the water content of the hydrous waste .
[0007]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the present invention will be described in more detail with reference to preferred embodiments.
Examples of the water-containing waste targeted by the present invention include food residues such as okara, sake lees, used rice cakes such as tea and coffee, food waste from households and restaurants, etc .; fish and livestock waste; vegetable waste, Agricultural waste such as vegetable and fruit squeezed rice cakes; various sludges such as activated sludge; pressurized flotation scum; manure of livestock such as cattle, pigs and chickens; various concentrated waste liquids. The type of water-containing waste is not particularly limited, and the water content is not limited.
INDUSTRIAL APPLICABILITY The present invention is suitable for drying hydrous waste containing objects having internal water such as sludge containing animals / plant residues and microorganisms.
[0008]
The feature of the present invention is that an inorganic salt or an inorganic acid (mineral acid) is allowed to coexist when the water-containing waste as described above is dried to remove moisture.
Inorganic salt used in the present invention, an alkali metal or alkaline earth metal salts of inorganic acids (mineral acids) are preferred, for example, N a 2 SO 4, NaNO 3, NaH 2 PO 4, Na 2 HPO 4, Na 3 PO 4 , CaCl 2 , Ca (NO 3 ) 2 , MgCl 2 and the like. Examples of the inorganic acid (mineral acid), Ri include the I acid. It is desirable to select the inorganic salt or the inorganic acid in consideration of the reuse of the dried hydrous waste.
[0009]
When drying the water-containing waste, in the form hydrous waste (hydrous solid, slurry solids, liquids, etc.) dryers Ru is used in accordance with the. For example, aeration box dryer, aeration band dryer, rotary dryer (usually vacuum type, cylindrical dryer itself rotates. There are direct heating type and indirect heating type heating methods), spray drying Accelerate drying by agitating the material to be dried by rotation of a stirring blade provided in a machine (spray dryer), evaporator, or non-rotating cylindrical dryer (in the case of the indirect heating method, the dryer wall and the direct heating method) And a stirring type vacuum dryer that pulverizes the dried material to be dried together with a heating medium (usually water vapor or heated air). A preferable dryer in the present invention is the above-described agitation type vacuum dryer that is hermetically sealed and does not leak malodor to the outside, and can be easily removed by adsorption of malodor or the like and can be recovered and processed. By using a vacuum dryer and adjusting the degree of vacuum, for example, it is possible to dry the hydrated waste at a low temperature of about 50 ° C. The operating conditions of the vacuum dryer are not particularly limited, and can be set as appropriate according to the water content of the water-containing waste.
[0010]
When the water-containing waste is vacuum dried, the amount of inorganic salt or acid used is adjusted according to the water content of the water-containing waste. Usually, the inorganic salt or the inorganic acid is preferably used in an amount of 0.001 to 10% by weight, more preferably 0.01 to 10% by weight, based on the water content of the hydrous waste. If the water-containing waste contains animals / plants and microorganisms, or if solids that absorb moisture are contained inside, the above amount may be further increased by about 10 to 50% by weight. preferable.
Inorganic salts or inorganic acids can be added to hydrous wastes either by mixing and dissolving them in hydrous waste in advance and then putting them in a vacuum dryer, or by adding hydrous wastes in a vacuum dryer. A salt or an inorganic acid may be added and dissolved.
[0011]
By using a vacuum dryer, the recovered water can be reused by being treated as it is or if necessary, or discharged into a river. On the other hand, the dried powdery waste can be reused as feed or fertilizer depending on the type.
[0012]
【Example】
The present invention will be specifically described below with reference to examples and comparative examples.
[0013]
Example 1 and Comparative Example 1
The following hydrated waste was dried using a stirring type cylindrical vacuum dryer (actual volume: 0.33 m 3 , heat transfer area: 4.99 m 2 , stirring power: 2.2 kw) whose schematic cross-sectional view is shown in FIG. .
200 kg of activated sludge cake having a water content of 83% by weight was put into a vacuum dryer, and then 0.5 kg of calcium chloride (CaCl 2 ) (0.3% by weight with respect to moisture) was added to start drying. The film was dried for 6 hours under conditions of a degree of vacuum of 75 mmHg (10 kPa) and an internal temperature of 55 ° C. The dried waste was powdery and the water content was 4.8% by weight.
Further, the same water-containing waste as described above was dried under the same conditions except that calcium chloride was not used. The moisture content of the dry waste was 28% by weight and powdering was insufficient. The total drying time until reaching the same water content as above was 11 hours.
[0014]
Example 2 and Comparative Example 2
Using the same vacuum dryer as in Example 1, 120 kg of vegetable scrap having a moisture content of 96% by weight was added, and then 0.3 kg of phosphoric acid (0.27% by weight with respect to moisture) was added. It was dried for 6 hours under the same conditions as in Example 1. The dry waste produced by the method of the present invention was powdery and had a moisture content of 8.2% by weight. On the other hand, the dry waste of the comparative example had a moisture content of 33% by weight, and the total drying time until reaching the same moisture content as above was 13 hours.
[0015]
【The invention's effect】
According to the present invention described above, drying of hydrous waste, which can be efficiently dried and dried waste can be recycled even when the hydrous waste contains plants or microorganisms having internal water. A method is provided.
[Brief description of the drawings]
FIG. 1 is a schematic sectional view of an example of a stirring type vacuum dryer used in the present invention.
Claims (2)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2002305408A JP4031345B2 (en) | 2002-10-21 | 2002-10-21 | Method for drying hydrous waste |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2002305408A JP4031345B2 (en) | 2002-10-21 | 2002-10-21 | Method for drying hydrous waste |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JP2004136239A JP2004136239A (en) | 2004-05-13 |
| JP4031345B2 true JP4031345B2 (en) | 2008-01-09 |
Family
ID=32452516
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2002305408A Expired - Lifetime JP4031345B2 (en) | 2002-10-21 | 2002-10-21 | Method for drying hydrous waste |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP4031345B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| NO20051723A (en) * | 2005-04-07 | 2006-05-22 | Bns Container As | Procedure for burglary protection of a container |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102942426A (en) * | 2012-11-16 | 2013-02-27 | 蒋斌 | Vacuum dehydration device for granulating machine of biotic organic fertilizer |
-
2002
- 2002-10-21 JP JP2002305408A patent/JP4031345B2/en not_active Expired - Lifetime
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| NO20051723A (en) * | 2005-04-07 | 2006-05-22 | Bns Container As | Procedure for burglary protection of a container |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2004136239A (en) | 2004-05-13 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US5196043A (en) | Delayed, exothermic, alkaline sterilization method for treating wastewater sludges | |
| JP5112698B2 (en) | Method and apparatus for producing nitrogen fertilizer from organic waste | |
| JP2742016B2 (en) | Method and apparatus for composting organic matter having high moisture content | |
| KR100651066B1 (en) | Apparatus and method for producing matured compost-like material | |
| JP2001226180A (en) | Kitchen waste recycling system and method | |
| JP4031345B2 (en) | Method for drying hydrous waste | |
| KR101110143B1 (en) | Food waste treatment device | |
| KR100792166B1 (en) | Waste and waste treatment methods containing organic matter | |
| KR101767256B1 (en) | A food garbage treating method for zero discharge of food waste water | |
| JP2003019472A (en) | Liquid-containing waste treatment method | |
| KR200484792Y1 (en) | Cow-pat treatment apparatus | |
| KR100589712B1 (en) | Handling system of saprophytic waste matter and the method thereof | |
| KR100864944B1 (en) | Organic Waste Treatment Using Lump Quicklime | |
| JP2000327465A (en) | How to use unused marine waste | |
| TWI405745B (en) | Method for producing water - soluble quick - acting organic fertilizer with activated sludge | |
| EP2653456A1 (en) | The method of obtaining the mineral-organic fertilizer from waste agricultural biogas digestate | |
| JPS6317986A (en) | Soil improving material and production thereof | |
| JP2607304Y2 (en) | Drying equipment for hydrous organic matter | |
| KR102863569B1 (en) | Heat-drying organic waste treatment device | |
| JP3079176B2 (en) | Solid fermentation equipment | |
| JPH10291877A (en) | Production method of organic sludge fertilizer | |
| JPS6138159B2 (en) | ||
| JP3140298U (en) | Organic waste treatment equipment | |
| JP2000229276A (en) | Liquid-containing waste treatment method | |
| CN117964430A (en) | Method for pollution-free treatment of organic wastewater, animal and plant residues and feces |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20050705 |
|
| A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20070409 |
|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20070417 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20070618 |
|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20070710 |
|
| A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20070910 |
|
| TRDD | Decision of grant or rejection written | ||
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20071009 |
|
| A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20071018 |
|
| R150 | Certificate of patent or registration of utility model |
Ref document number: 4031345 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20101026 Year of fee payment: 3 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20101026 Year of fee payment: 3 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20111026 Year of fee payment: 4 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20111026 Year of fee payment: 4 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20121026 Year of fee payment: 5 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20131026 Year of fee payment: 6 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20131026 Year of fee payment: 6 |
|
| S533 | Written request for registration of change of name |
Free format text: JAPANESE INTERMEDIATE CODE: R313533 |
|
| FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20131026 Year of fee payment: 6 |
|
| R350 | Written notification of registration of transfer |
Free format text: JAPANESE INTERMEDIATE CODE: R350 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| S531 | Written request for registration of change of domicile |
Free format text: JAPANESE INTERMEDIATE CODE: R313531 |
|
| S533 | Written request for registration of change of name |
Free format text: JAPANESE INTERMEDIATE CODE: R313533 |
|
| R350 | Written notification of registration of transfer |
Free format text: JAPANESE INTERMEDIATE CODE: R350 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| EXPY | Cancellation because of completion of term |