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JP2001231394A - Method for culturing capitella sp.1 for cleaning organic substance sludge and method for cleaning organic substance sludge - Google Patents

Method for culturing capitella sp.1 for cleaning organic substance sludge and method for cleaning organic substance sludge

Info

Publication number
JP2001231394A
JP2001231394A JP2000050762A JP2000050762A JP2001231394A JP 2001231394 A JP2001231394 A JP 2001231394A JP 2000050762 A JP2000050762 A JP 2000050762A JP 2000050762 A JP2000050762 A JP 2000050762A JP 2001231394 A JP2001231394 A JP 2001231394A
Authority
JP
Japan
Prior art keywords
sludge
organic
strawberry
seawater
cultivation
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.)
Granted
Application number
JP2000050762A
Other languages
Japanese (ja)
Other versions
JP4049505B2 (en
Inventor
Hiroaki Tsutsumi
裕昭 堤
Shigeru Kadotani
門谷  茂
Hiroki Takahashi
浩樹 高橋
Keisuke Shozen
圭祐 少前
Takako Tokuda
貴子 徳田
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.)
Mercian Corp
Marine Bio Co Ltd Japan
Original Assignee
Mercian Corp
Marine Bio Co Ltd Japan
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 Mercian Corp, Marine Bio Co Ltd Japan filed Critical Mercian Corp
Priority to JP2000050762A priority Critical patent/JP4049505B2/en
Publication of JP2001231394A publication Critical patent/JP2001231394A/en
Application granted granted Critical
Publication of JP4049505B2 publication Critical patent/JP4049505B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/80Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
    • Y02A40/81Aquaculture, e.g. of fish

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  • Farming Of Fish And Shellfish (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for more efficiently cleaning an organic substance sludge by preculturing a large amount of Capitella sp.1 as benthos and positively scattering the cultured Capitella sp.1 on the organic substance sludge in the autumn when this organism can live. SOLUTION: The method for culturing Capittela sp.1 for cleaning an organic substance sludge is characterized in that a feed is periodically scattered on a Capitella sp.1 culture substrate and Capitella sp.1 stored in a seawater tank, and Capitella sp.1 is cultured at 5-25 deg.C with aeration until Capitella sp.1 density reaches 4×106 organisms/m2. The method for cleaning an organic substance sludge is characterized in that the culture substrate containing Capitella sp.1 in high density obtained by the culturing method is scattered on a deposited sludge in a target sea area to be cleaned and the organic substance sludge is cleaned by utilizing the organic substance consumption force of Capitella sp.1.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、有機物汚泥浄化用
イトゴカイの培養方法および有機物汚泥の浄化方法に関
する。さらに詳しくいえば、養魚場で撒布される餌の残
滓や魚の排泄物(糞)に起因して海底に多量に堆積して
いる有機物汚泥を効率的に浄化するために使用されるイ
トゴカイの高密度培養方法、およびその方法で培養され
たイトゴカイを用いる有機物汚泥の浄化方法に関する。
TECHNICAL FIELD The present invention relates to a method for cultivating Itokai for purifying organic sludge and a method for purifying organic sludge. More specifically, the high-density density of the cod that is used to efficiently purify large amounts of organic sludge deposited on the seabed due to food residues and fish excreta (feces) sprayed at fish farms The present invention relates to a culture method and a method for purifying organic sludge using a strawberry grown by the method.

【0002】[0002]

【従来技術とその課題】日本各地の沿岸域においてはハ
マチやタイを中心とした養殖漁業が普及しているが、養
漁場で大量に撒かれる餌はその10〜20%しか養殖魚
の成長に寄与していないといわれている(「残海養殖と
自家汚染」(日本水産学会編),42〜51(1977),
恒星社厚生閣)。養漁場で撒かれる有機物の80〜90
%は、溶存物質や懸濁物質となったり魚の代謝活動で栄
養塩となって養漁場周辺の海域に流出し、また糞や残滓
となって海底に堆積する。海底に堆積した大量の有機物
は高水温期(夏季)には嫌気的な分解過程により有害な
硫化水素を発生し、海底は生物が生息できない大量の有
機物汚泥(ヘドロ)で汚染される。この有機物汚泥をい
かに除去するかは、養殖漁業の維持発展にとって大きな
問題である。
2. Description of the Related Art While aquaculture and fishery, mainly hamachi and thailand, are widespread in coastal areas around Japan, only 10 to 20% of bait scattered in fish farms contributes to the growth of cultured fish. (“Remaining Sea Culture and Self-Pollution” (edited by the Japanese Fisheries Society), 42-51 (1977),
Koseisha Koseikaku). 80-90 of organic matter sprinkled in fish farm
% Becomes dissolved or suspended matter, or becomes a nutrient due to the metabolic activity of fish, flows out to the sea area around the fishery, and deposits on the sea floor as feces and residue. A large amount of organic matter deposited on the sea floor generates harmful hydrogen sulfide during the high water temperature period (summer) due to an anaerobic decomposition process, and the sea floor is contaminated with a large amount of organic sludge (sludge) that cannot inhabit living things. How to remove this organic sludge is a major problem for the maintenance and development of aquaculture.

【0003】有機物汚泥を除去する対策としては、これ
まで海底に堆積した有機物汚泥の浚渫や覆砂、石灰の投
入、湾口部の掘削によって海水の交換を促進し海底の有
機物の分解を促進する方法等が提案されている。しか
し、これらの方法は、海域の地形・性状ひいては環境全
体を変えるものであり、生態系全体に及ぼす影響につい
ては明らかではなく、さらに莫大な費用がかかることか
ら、現実的な対策ではない。一方、海底のヘドロには海
水温度が低下する秋季になると対流現象により酸素が供
給されるようになるため、いずれ有機物汚泥(ヘドロ)
を栄養源とするベントス(底生生物)の作用により浄化
される。
As a countermeasure for removing organic matter sludge, a method of promoting the exchange of seawater and promoting the decomposition of organic matter on the seafloor by dredging, covering with sand, charging lime, and excavating a bay mouth so far has been carried out. Etc. have been proposed. However, these methods change the terrain and characteristics of the sea area, and thus the entire environment, and their effects on the entire ecosystem are not clear. Further, these methods are enormous and are not realistic measures. On the other hand, in the fall when the seawater temperature falls, oxygen is supplied to the sludge on the seabed by the convection phenomenon.
It is purified by the action of bentos (benthic organisms), which use as a nutrient source.

【0004】[0004]

【課題を解決するための手段】本発明者らはベントス
(底生生物)を予め大量に培養しておいて、これを、生
物が生息できる秋期に積極的に有機物汚泥の上に撒くこ
とにより効率的に有機物汚泥が浄化できるものと考えて
検討した。ベントス(底生生物)としては、スピオ科や
小型多毛類等が知られているが、中でもイトゴカイ(Ca
pitella sp.1)は有機物汚染地域に高密度に出現し、ヘ
ドロ環境条件の回復期には爆発的に増殖することが知ら
れている(J. Mar. Res.,32,253-184(1974)。そこでイ
トゴカイの大量培養について鋭意研究を重ね本発明を完
成した。
Means for Solving the Problems The present inventors have previously cultured a large amount of benthos (benthic organism), and then actively scattered this on organic sludge in the autumn when the organism can inhabit. We considered that organic sludge could be purified efficiently. As benthos (benthic organisms), spioceae and small polychaetes are known.
It is known that pitella sp.1) appears at high density in areas contaminated with organic matter and proliferates explosively during the recovery period of sludge environmental conditions (J. Mar. Res., 32, 253-184 (1974)). Accordingly, the present inventors have conducted intensive studies on the mass cultivation of Itokai and completed the present invention.

【0005】すなわち、本発明は以下の有機物汚泥浄化
用イトゴカイの培養方法および有機物汚泥の浄化方法を
提供するものである。 1)海水槽に収容したイトゴカイ培養基質とイトゴカイ
に、餌を定期的に撒布して5〜25℃の温度で通気しな
がらイトゴカイ密度4×106個体/m2以上まで培養す
ることを特徴とする有機物汚泥浄化用イトゴカイの培養
方法。 2)イトゴカイ培養基質とイトゴカイとを収納したプラ
スチック製容器を海水槽の底部に載置して培養する前記
1に記載の有機物汚泥浄化用イトゴカイの培養方法。 3)餌を有機炭素含有量換算で1.0gC/m2・日〜2.8
gC/m2・日の量撒布する前記1に記載の有機物汚泥
浄化用イトゴカイの培養方法。 4)海水槽のアンモニア濃度を1.2mM以下に維持して
培養する前記1に記載の有機物汚泥浄化用イトゴカイの
培養方法。 5)イトゴカイ培養基質とイトゴカイを、プラスチック
製容器の内面に敷いたプラスチック製シートの上に収納
して培養を行なう前記2に記載の有機物汚泥浄化用イト
ゴカイの培養方法。 6)培養基質が細砂である前記1または2に記載の有機
物汚泥浄化用イトゴカイの培養方法。 7)プラスチック製容器、またはプラスチック製容器と
プラスチック製シートとして、培養後のイトゴカイを有
機物汚泥海水域に撒布する作業に耐える強度を有するも
のを使用する前記2または5に記載の有機物汚泥浄化用
イトゴカイの培養方法。 8)前記1乃至7のいずれかに記載の方法により得られ
たイトゴカイを高密度に含む培養基質を、浄化対象の海
水域の堆積汚泥上に撒布しイトゴカイの有機物消費力を
利用して有機物汚泥を浄化することを特徴とする有機物
汚泥の浄化方法。
That is, the present invention provides the following method for cultivating a coconut oyster for purifying organic sludge and a method for purifying organic sludge. 1) It is characterized in that bait is regularly sprayed on the cultivation substrate and locust moss contained in the seawater tank, and cultivation is performed at a density of 4 × 10 6 individuals / m 2 or more while aerating at a temperature of 5 to 25 ° C. Cultivation method of strawberry cultivation for purification of organic sludge. 2) The method of cultivating organic sludge purifying strawberry as described in 1 above, wherein a plastic container containing a strawberry cultivation substrate and strawberry is placed on the bottom of a seawater tank for culturing. 3) The feed is 1.0 gC / m 2 · day to 2.8 in terms of organic carbon content.
2. The method for cultivating a cocoon for purifying organic sludge as described in 1 above, wherein the cultivation is carried out in an amount of gC / m 2 · day. 4) The method for cultivating a cocoon for purifying organic sludge as described in 1 above, wherein the cultivation is performed while maintaining the ammonia concentration in the seawater tank at 1.2 mM or less. 5) The method for cultivating a strawberry for purification of organic sludge as described in 2 above, wherein the strawberry cultivation substrate and the strawberry are stored on a plastic sheet spread on the inner surface of a plastic container and cultured. 6) The method for cultivating Itokai for purifying organic sludge as described in 1 or 2 above, wherein the culture substrate is fine sand. 7) The organic sludge purifying organic sludge as described in 2 or 5 above, wherein a plastic container or a plastic container and a plastic sheet having a strength enough to withstand the operation of dispersing cultured strawberry in an organic sludge seawater area is used. Culture method. 8) Spreading a culture substrate containing the nested locusts obtained by the method according to any one of the above 1 to 7 at a high density on sedimentary sludge in a seawater area to be purified, and utilizing the organic matter consumption power of nested nests A method for purifying organic sludge, comprising purifying odor.

【0006】以下、本発明を詳しく説明する。 (1)イトゴカイ イトゴカイは小型多毛類(環形動物)に属し、成体の体
長が10mm程度、最大部分の径が1mm程度の糸状の
生物である。海底環境が著しく嫌気化した夏季には増殖
速度が極度に鈍化するが、秋季から冬季にかけて海底環
境が回復し、水温10〜15℃、底層水の溶存酸素が飽
和またはそれに近い条件下になると、約4〜6週間で成
体に成長し繁殖を繰り返すことによって爆発的な増殖能
力を示す。その増殖の過程で有機物汚泥中の有機物を栄
養源とするため汚泥が分解除去される。
Hereinafter, the present invention will be described in detail. (1) Itokai Ito belongs to small polychaetes (annelids) and is a thread-like organism with an adult body length of about 10 mm and a maximum diameter of about 1 mm. In summer, when the seafloor environment is significantly anaerobic, the growth rate is extremely slowed down, but the seafloor environment recovers from autumn to winter, when the water temperature is 10 to 15 ° C, and the dissolved oxygen in the bottom water becomes saturated or close to it, It shows an explosive proliferative ability by repeating adult growth and reproduction in about 4 to 6 weeks. During the growth process, the sludge is decomposed and removed because the organic matter in the organic sludge is used as a nutrient source.

【0007】本発明においては、海底環境が回復する秋
から冬に予め培養しておいた大量のイトゴカイを、有機
物汚泥上に撒布することにより、自然現象では起こり得
ない高密度個体群を短期間に発生させて、海底に堆積し
た有機物汚泥を効率的に浄化する。本発明では養漁場
(養殖いけす)の海底に堆積している有機物汚泥を効率
的に浄化するためイトゴカイを培養基質中の密度で4×
106個体/m2以上、好ましくは5×106個体/m2
上に培養してこれを撒布する。
[0007] In the present invention, a large amount of strawberry cultivated in advance from autumn to winter when the seafloor environment recovers is sprayed on organic sludge, so that a high-density population that cannot occur by natural phenomena can be obtained for a short period of time. To efficiently purify organic sludge deposited on the sea floor. In the present invention, in order to efficiently purify organic sludge deposited on the seabed of a fish farm (aquaculture fish), a strawberry oyster is grown at a density of 4 × in a culture substrate.
The cells are cultivated to 10 6 individuals / m 2 or more, preferably 5 × 10 6 individuals / m 2 or more, and are spread.

【0008】なお、本明細書おいては、イトゴカイ培養
密度を単位面積当たりで表示しているが、これは単に表
面のみに存在するイトゴカイの数を意味するのではな
く、培養密度測定用に採取したサンプル中のイトゴカイ
(イトゴカイは表面から約2cmの深さにのみに生息す
る)の全数を、サンプリングコアの面積で徐した値を意
味する。
[0008] In the present specification, the cultivation density of the locust is shown per unit area, but this does not mean simply the number of locusts present only on the surface, but is used to measure the cultivation density. This means a value obtained by subtracting the total number of nests (the nests that live only at a depth of about 2 cm from the surface) in the sample by the area of the sampling core.

【0009】(2)イトゴカイの培養方法 本発明においては、海水槽に収容したイトゴカイ培養基
質とイトゴカイに、餌を定期的に撒布してイトゴカイの
培養を行なう。この培養は、所定の密度以上に大量培養
されたイトゴカイを浄化対象の海水域に撒布する際の作
業性を考慮して、作業者が取り扱いやすい大きさのプラ
スチック製などの容器を載置し、その容器中で行なうこ
とが好ましい。餌は易分解性の有機物であればよい。例
えば、魚用配合飼料、モイストペレットなどを使用でき
る。これを所定の量定期的(通常1日1回)に海水槽の
上部から撒いて給餌する。
(2) Cultivation Method of the Strawberry In the present invention, the bait is regularly sprayed on the Strawberry culture substrate and the Strawberry that are accommodated in the seawater tank to culture the Strawberry. In this culture, in consideration of the workability when spraying a cultivated strawberry in a sea area to be purified in a large amount at a predetermined density or more, a container made of plastic or the like having a size that is easy for an operator to handle is placed, It is preferably carried out in that container. The feed may be any easily decomposable organic substance. For example, a mixed feed for fish, a moist pellet, or the like can be used. This is scattered from the upper part of the seawater tank at a predetermined amount regularly (usually once a day) for feeding.

【0010】培養温度は5〜25℃、好ましくは10〜
20℃とし、培養中はエアーポンプにより適宜通気を行
ない、海水中の溶存酸素濃度を飽和状態に保つことが好
ましい。培養に用いるイトゴカイは、幼生でも成体でも
よい。イトゴカイ幼生及び成体は自然界から採取したも
のを使用する。幼生の場合は採取した抱卵雌を選別し
て、これを1〜数個体ずつ海水を入れたビーカーに数日
間放置した後、浮遊してくる幼生を集めて用いる。
The culture temperature is 5 to 25 ° C., preferably 10 to 25 ° C.
It is preferable that the temperature is set to 20 ° C., and that aeration is appropriately performed by an air pump during the culture to keep the dissolved oxygen concentration in the seawater in a saturated state. Strawberries used for culture may be larvae or adults. The larvae and adult larvae collected from nature are used. In the case of larvae, the collected incubating females are selected and left for one to several individuals in a beaker filled with seawater for several days, and then the floating larvae are collected and used.

【0011】培養基質は、イトゴカイの培養に適したも
のであれば特に限定されないが、細い砂(細砂)が好ま
しく用いられる。細砂を使用するとイトゴカイはその隙
間に潜り込んだ状態で増殖するため、撒布直後に海底に
生息する魚類に捕食され難いという利点がある。細砂と
しては、粒径が150μm以下で、中央粒径値が50〜
80μm程度のものがよい。このような細砂としては一
般に市販されているものが使用できる。
[0011] The culture substrate is not particularly limited as long as it is suitable for cultivation of Itokai, but fine sand (fine sand) is preferably used. When fine sand is used, nesting creatures proliferate while sunk into the gaps, and have the advantage that they are less likely to be eaten by fish living on the seabed immediately after being scattered. As fine sand, the particle size is 150 μm or less, and the median particle size is 50 ~
It is preferably about 80 μm. As such fine sand, generally available ones can be used.

【0012】培養容器としては、有機物汚泥海水域に撒
布する作業に耐える強度と作業に手頃な大きさのプラス
チック製(例えばポリエチレン、ポリプロピレン、ポリ
塩化ビニル等のポリオレフィン製のもの)が使用される
が、撒布作業後海水中に放置しても微生物の作用により
分解される生分解性プラスチック製の容器を使用するこ
とが好ましい。容器としては、一辺が10〜30cm、
深さが5〜10cm程度の矩形の箱型容器が適当であ
る。
As the culture vessel, a plastic (for example, one made of polyolefin such as polyethylene, polypropylene, polyvinyl chloride, etc.) is used which is strong enough to withstand the operation of spraying the organic sludge in the seawater and is large enough for the operation. It is preferable to use a biodegradable plastic container that is decomposed by the action of microorganisms even when left in seawater after the spraying operation. As a container, one side is 10 to 30 cm,
A rectangular box-shaped container having a depth of about 5 to 10 cm is suitable.

【0013】培養容器に直接培養基質を入れて培養を行
なうと、培養時に受ける海水の圧力により、培養基質が
容器にこびりつき、撒布作業の障害となる。そこで容器
の内面にプラスチック製シートを敷いてその上で培養す
ることが好ましい。この場合には、培養後にイトゴカイ
を傷つけることなく容器からイトゴカイを高密度に含む
培養基質をシート毎に回収し撒布作業を行なうことがで
きる。プラスチック製シートの材料としては先に容器に
ついて説明したと同様のものが用いられる。培養は、イ
トゴカイが所定の高密度(4×106個体/m2以上)に
なるまで行なう。所定の密度まで増殖しているか否か
は、経時的にサンプリングして実体顕微鏡下でイトゴカ
イ数を計測して判断する。
When a culture substrate is directly put into a culture container for culturing, the pressure of seawater received during the culture causes the culture substrate to stick to the container, which hinders the spraying operation. Therefore, it is preferable to spread a plastic sheet on the inner surface of the container and culture on the sheet. In this case, it is possible to collect the culture substrate containing the locust oysters at a high density from the container for each sheet without damaging the strawberry during the culturing, and to perform the spreading operation. As the material of the plastic sheet, the same material as described above for the container is used. The cultivation is continued until the density of the strawberry grows to a predetermined high density (4 × 10 6 individuals / m 2 or more). Whether or not the cells have grown to a predetermined density is determined by sampling over time and measuring the number of locusts under a stereoscopic microscope.

【0014】(i)餌の撒布量 培養基質中の有機炭素含有量が高くなるとイトゴカイの
培養環境が悪化する。すなわち、培養基質中の有機炭素
含有量が2.8gC/m2を超えると、イトゴカイの増殖に
悪影響を及ぼす。したがって培養基質中の有機炭素含有
量が2.8gC/m2以下、好ましくは2.5gC/m2程度以
下となる量の餌(易分解性有機物)を撒布するのがよ
い。撒布量としては、培養基質中の有機炭素含有量換算
で1.0〜2.8gC/m2、好ましくは1.5〜2.5gC/m2
さらに好ましくは1.8〜2.2gC/m2程度である。
(I) Amount of Food Spread When the organic carbon content in the culture substrate increases, the cultivation environment of the straggler deteriorates. That is, if the organic carbon content in the culture substrate exceeds 2.8 gC / m 2 , it will adversely affect the growth of strawberry. Therefore, it is good to sprinkle bait (easy decomposable organic matter) in such an amount that the organic carbon content in the culture substrate is 2.8 gC / m 2 or less, preferably about 2.5 gC / m 2 or less. The sprayed amount, 1.0~2.8gC / m 2 in an organic carbon content in terms of the culture substrate, preferably 1.5~2.5gC / m 2,
More preferably 1.8~2.2gC / m 2 approximately.

【0015】(ii)培養海水中のアンモニア濃度 イトゴカイを培養する海水が汚染されるとイトゴカイの
増殖に悪影響を及ぼす。海水の汚染は有機物の分解に伴
い発生するアンモニア濃度を指標にして判断することが
できるが、イトゴカイの増殖に影響を与えないアンモニ
ア濃度は、1.2mmol/L(1.2mM)以下である。海水中
のアンモニア濃度をイトゴカイの培養に適したレベルに
保つためには、海水槽の海水を一定間隔で一部交換する
ことが考えられるが、増殖するイトゴカイは、数時間程
度の浮遊幼生期を持つので海水の交換によって幼生を捨
ててしまう危険がある。したがって、海水は可能な限り
交換しないことが好ましい。
(Ii) Ammonia concentration in the culture seawater Contamination of the seawater for cultivation of the mosquitoes adversely affects the growth of mosquitoes. Seawater contamination can be determined by using the ammonia concentration generated as a result of the decomposition of organic matter as an index. The ammonia concentration that does not affect the growth of the strawberry is 1.2 mmol / L (1.2 mM) or less. In order to maintain the ammonia concentration in seawater at a level suitable for cultivation of nests, it is conceivable to exchange some of the seawater in the sea tank at regular intervals. There is a risk that the larvae will be thrown away by exchanging seawater. Therefore, it is preferable that seawater is not changed as much as possible.

【0016】海水を高頻度に交換せずに、アンモニア濃
度を所定のレベルに維持する方法としては、高密度にイ
トゴカイが増殖するまで、アンモニア濃度が1.2mM以
下の状態に保たれるよう相対的に大量の海水を用いるこ
とが好ましい。そうすることにより海水を交換する必要
がなく作業性が向上し、イトゴカイの損失を防止でき、
効率的にイトゴカイを培養することができる。
As a method for maintaining the ammonia concentration at a predetermined level without frequently exchanging seawater, there is a method for maintaining the ammonia concentration at 1.2 mM or less until the nests grow high density. It is preferable to use a large amount of seawater. By doing so, it is not necessary to change the seawater, workability is improved, and it is possible to prevent the loss of Itokai,
It is possible to efficiently cultivate a strawberry.

【0017】[0017]

【実施例】以下、試験例および実施例を挙げて本発明を
さらに詳しく説明するが、本発明は下記の例に限定され
るものではない。
EXAMPLES The present invention will be described in more detail with reference to Test Examples and Examples, but the present invention is not limited to the following Examples.

【0018】試験例1:餌供給量のイトゴカイ成長に対
する影響 培養基質としての細砂(株式会社熊本硅砂鉱業製、K−
8,中央粒径:60μm)900gと海水2リットルと
を、ポリ塩化ビニル製の4個のプラスチック製容器(蝶
プラ工業株式会社製、30×20×10cm)に収納
し、さらに各々にイトゴカイ幼生500個体を入れた。
これら培養容器を18.0℃に設定した恒温海水槽に入れ、
エアーポンプ(直径3.0cm)で通気した。餌として、
ハマチ養殖用のモイストペレット(メルシャン株式会社
製;有機炭素含有率44%)を粉末にしたものを1日に
1回添加した。給餌量はイトゴカイの個体成長やコロニ
ー全体の増殖に合わせて増加させた。給餌量の違う以下
の3つの試験区L、M、Hを設け、培養開始から6週間
後のイトゴカイの個体群密度を測定し、その平均値を求
めた。
Test Example 1: Influence of Feeding Amount on Strawberry Growing Fine Sand as Culture Substrate (K-Kumamoto Silica Sand Co., Ltd., K-
(8, median particle diameter: 60 μm) 900 g and 2 liters of seawater were stored in four plastic containers made of polyvinyl chloride (30 × 20 × 10 cm, manufactured by Chopura Kogyo Co., Ltd.) 500 individuals were placed.
Put these culture vessels in a constant temperature seawater tank set at 18.0 ° C,
It was ventilated with an air pump (3.0 cm in diameter). As bait,
Powdered moist pellets for Hamachi cultivation (manufactured by Mercian Co .; organic carbon content: 44%) were added once a day. The amount of feed was increased in accordance with the growth of the pods and the growth of the whole colony. The following three test plots L, M, and H with different feeding amounts were provided, and the population density of the mosquitoes 6 weeks after the start of the culture was measured, and the average value was obtained.

【0019】給餌量: 試験区L:第1週目0.1g、第2週目〜第8週目0.2g、 試験区M:第1週目0.1g、第2週目0.2g、第3〜8週
目0.3g、 試験区H:第1週目0.1g、第2週目0.2g、第3〜4週
目0.3g、第5〜6週目0.4g。
Feeding amount: Test group L: 0.1 g for the first week, 0.2 g for the second to eighth weeks, test group M: 0.1 g for the first week, 0.2 g for the second week, third to 0.3 g at the 8th week, test plot H: 0.1 g at the first week, 0.2 g at the second week, 0.3 g at the 3rd and 4th weeks, 0.4 g at the 5th to 6th weeks.

【0020】イトゴカイの個体群密度の測定は、培養基
質を採取してローズベンガルを溶かした10%ホルマリ
ン溶液で固定した後、125μmメッシュのふるいにか
け、実体顕微鏡下で計測して行なった。培養基質の単位
面積当たりで換算した有機炭素含有量は以下の計算式か
ら求めた。
The population density of Itokai was measured by collecting a culture substrate, fixing it with a 10% formalin solution in which rose bengal was dissolved, and sieving through a 125 μm mesh sieve to measure under a stereoscopic microscope. The organic carbon content converted per unit area of the culture substrate was determined by the following formula.

【数1】有機炭素含有量(gC/m2)=餌量(g)×1
0000(cm2)/600(cm2)×0.44 結果を表1に示す。
## EQU1 ## Organic carbon content (gC / m 2 ) = feed amount (g) × 1
0000 (cm 2 ) / 600 (cm 2 ) × 0.44 The results are shown in Table 1.

【0021】[0021]

【表1】 表 1 試験区 イトゴカイ個体群密度 有機炭素含有量 (個体数/10cm2 ) (gC/m2 L 3079 1.5 M 3989 2.2 H 442 2.9 [Table 1] Table 1 Test plot Strawberry population density Organic carbon content (number of individuals / 10 cm 2 ) (gC / m 2 ) L 3079 1.5 M 3989 2.2 H 442 2.9

【0022】表1から、高濃度に有機炭素を含む試験区
Hでは、イトゴカイ個体群密度が非常に低く、有機炭素
含有量が2.9gC/m2以上の場合には、イトゴカイの増
殖が阻害された。試験区Lおよび試験区Mでは、高いイ
トゴカイ個体群密度が得られ、イトゴカイの成長に好ま
しい餌の量は有機炭素含有量換算で、2.8gC/m2以下
であり、特に2.2gC/m2程度が好ましいこと分かる。
From Table 1, it can be seen that, in the test plot H containing a high concentration of organic carbon, the density of the codling population is very low, and when the organic carbon content is 2.9 gC / m 2 or more, the growth of codling is inhibited. Was. In the test plot L and the test plot M, a high density of the cod population was obtained, and the preferable amount of bait for the growth of the cod was not more than 2.8 gC / m 2 , especially about 2.2 gC / m 2 in terms of organic carbon content. Is preferable.

【0023】試験例2:海水中のアンモニア濃度のイト
ゴカイ成長に対する影響 試験例1と同じ培養基質900gと海水2リットルと
を、試験例1で用いたのと同様の4個のプラスチック製
容器(30×20×10cm)に入れ、それぞれイトゴ
カイ幼生500個体を入れた。培養容器は、18.0℃に設
定した恒温槽に入れ、エアーポンプ(直径3.0cm)で
通気した。餌として試験例1と同じハマチ養殖用のモイ
ストペレット粉末を1日に1回添加した。給餌量はイト
ゴカイの個体成長やコロニー全体の増殖に合わせて増加
させ、第1週目0.1g、第2週目0.2g、第3〜8週目0.
3gとした。培養は8週間行ない、その間、海水の交換
頻度を、週3回(試験区A)、週2回(試験区B)、週
1回(試験区C)及び2週間に1回(試験区D)に変え
た試験区(A、B、C、D)を設け、培養開始から4週
間後、6週間後、8週間後にイトゴカイコロニーの密度
および海水中のアンモニア濃度を試験例1と同様にして
測定し、その平均値を求めた。アンモニア濃度は、海水
交換時に海水0.25リットルをワットマン(Whatman)G
F/Fグラス・ファイバー・フィルターを用いてポンプ
で吸引ろ過し、得られたろ液のアンモニア濃度を自動栄
養塩濃度測定装置(Technicon II)を用いて測定した。
結果を表2(コロニー密度)および表3(アンモニア濃
度)に示す。
Test Example 2: Effect of Ammonia Concentration in Sea Water on Growth of Strawberry Inspection 900 g of the same culture substrate as in Test Example 1 and 2 liters of sea water were used in the same four plastic containers (30) as used in Test Example 1. × 20 × 10 cm), and 500 larvae of each larva were placed. The culture vessel was placed in a thermostat set at 18.0 ° C. and ventilated with an air pump (3.0 cm in diameter). As a bait, the same moist pellet powder for hamachi cultivation as in Test Example 1 was added once a day. The amount of feed was increased in accordance with the growth of the individual colonies and the growth of the whole colony, and 0.1 g in the first week, 0.2 g in the second week, and 0.1 g in the third to eighth weeks.
3 g. Culture was performed for 8 weeks, during which time the frequency of seawater exchange was changed three times a week (test zone A), twice a week (test zone B), once a week (test zone C), and once every two weeks (test zone D). ) Were provided, and after 4 weeks, 6 weeks, and 8 weeks from the start of the culture, the density of the cod colony and the ammonia concentration in seawater were determined in the same manner as in Test Example 1. It measured and the average value was calculated | required. Ammonia concentration was measured using 0.25 liters of seawater at the time of seawater exchange.
Suction filtration was performed with a pump using an F / F glass fiber filter, and the ammonia concentration of the obtained filtrate was measured using an automatic nutrient concentration measurement device (Technicon II).
The results are shown in Table 2 (colony density) and Table 3 (ammonia concentration).

【0024】[0024]

【表2】 表 2 培養期間(週) コロニー密度(個体数/m2 試験区A 試験区B 試験区C 試験区D 0 7,962 7,962 7,962 7,962 4 7,317×102 9,138×102 1,082×103 1,492×103 6 2,840×103 4,323×103 5,449×103 6,805×102 8 1,794×103 5,104×103 3,353×103 3,712×10 [Table 2] Table 2 Culture period (weeks) Colony density (number of individuals / m 2 ) Test plot A Test plot B Test plot C Test plot D 0 7,962 7,962 7,962 7,962 4 7,317 × 10 2 9,138 × 10 2 1,082 × 10 3 1,492 × 10 3 6 2,840 × 10 3 4,323 × 10 3 5,449 × 10 3 6,805 × 10 2 8 1,794 × 10 3 5,104 × 10 3 3,353 × 10 3 3,712 × 10

【0025】[0025]

【表3】 表 3 培養期間(週) アンモニア濃度(mM) 試験区A 試験区B 試験区C 試験区D 0 0.25 0.25 0.25 0.25 4 1.00 0.62 0.98 0.45 6 1.11 0.85 1.75 1.24 8 0.96 0.89 2.19 6.41 [Table 3] Table 3 Culture period (weeks) Ammonia concentration (mM) Test plot A Test plot B Test plot C Test plot D 0 0.25 0.25 0.25 0.25 4 1.00 0.62 0.98 0.45 6 1.11 0.85 1.75 1.24 8 0.96 0.89 2.19 6.41

【0026】表2及び表3から、海水交換頻度の低い試
験区Dは、培養開始後4週目までは最もコロニー密度が
高いが、その後、コロニー密度は減少しており、培養開
始後6週目のアンモニア濃度は1.24mMであった。試験
区Cでは、培養開始後6週目まではコロニー密度の増加
がみられたが、その後、減少し、培養開始後6週目から
8週目のアンモニア濃度は1.75〜2.19mMであった。試
験区AおよびBでは、アンモニア濃度は1.11mM以下で
あったことから、イトゴカイの増殖に影響を与えないア
ンモニア濃度は、1.24mM以下であることが分かる。
From Tables 2 and 3, it can be seen from the test plot D having the lowest frequency of seawater exchange that the colony density was the highest up to 4 weeks after the start of the culture, but thereafter, the colony density decreased, and the colony density was 6 weeks after the start of the culture. The ammonia concentration in the eye was 1.24 mM. In test plot C, the colony density increased up to 6 weeks after the start of the culture, but then decreased, and the ammonia concentration from the 6th week to the 8th week after the start of the culture was 1.75 to 2.19 mM. In the test plots A and B, since the ammonia concentration was 1.11 mM or less, it can be seen that the ammonia concentration that does not affect the growth of the mosquitoes is 1.24 mM or less.

【0027】実施例 底面積10m2の円形の海水槽に海水を4000リット
ル(深さ約40cm)入れ、ここに内面にビニール袋を
敷き、その上に培養基質の細砂(株式会社熊本硅砂鉱業
製、K−8,中央粒径:60μm)を深さ1cmとなる
ように入れ、イトゴカイ幼生を500個入れた110個
のポリ塩化ビニル製プラスチック容器(蝶プラ工業株式
会社製、30×20×10cm)を沈めて、海水温度1
0〜20℃の範囲内で海水槽の下部2箇所からエアーポ
ンプで通気して海水中の溶存酸素濃度を飽和状態に保っ
た。
EXAMPLE A 4000 liter (approximately 40 cm deep) seawater was placed in a circular seawater tank with a bottom area of 10 m 2 , a plastic bag was laid on the inside, and fine sand of a culture substrate (Kumamoto Silica Sand Mining Co., Ltd.) was placed on top of it. , K-8, median particle size: 60 μm) to a depth of 1 cm, and 110 plastic containers made of polyvinyl chloride containing 500 larvae of Itokai (30 × 20 × 10cm) and seawater temperature 1
The dissolved oxygen concentration in the seawater was kept in a saturated state by ventilating the lower two portions of the seawater tank with an air pump within the range of 0 to 20 ° C.

【0028】餌としてハマチ養殖用の配合飼料(サンマ
リーンKG、メルシャン株式会社製)(有機炭素含有率
約40%)を粉末にしたものを与えた。1日に1回、海
水槽の水上に撒いて自然に沈降させることによって給餌
した。給餌量は、40〜60g/日とした。これは有機
炭素含有量換算で海水槽底面あたり約1.6〜2.4gC/m
2に相当する。海水槽中の海水をワットマン(Whatman)
GF/Fグラス・ファイバー・フィルターを用いてポン
プで吸引ろ過し、得られたろ液のアンモニア濃度を自動
栄養塩濃度測定装置(Technicon II)を用いて測定し
た。42日間の培養終了後の海水中のアンモニア濃度は
0.12mMであり、イトゴカイの増殖に影響を与えない1.
2mM以下に抑えられていた。
As a feed, a powdered compound feed for hamachi cultivation (Sun Marine KG, manufactured by Mercian Co., Ltd.) (organic carbon content: about 40%) was given. Once a day, they were fed by sprinkling on the water in a sea tank and allowing them to settle naturally. The feeding amount was 40 to 60 g / day. This is approximately 1.6 to 2.4 gC / m per sea tank bottom in terms of organic carbon content.
Equivalent to 2 . Whatman, seawater in a sea tank
The filtrate was suction-filtered using a GF / F glass fiber filter, and the ammonia concentration of the obtained filtrate was measured using an automatic nutrient concentration measuring device (Technicon II). After 42 days of culture, the ammonia concentration in seawater is
0.12 mM, which does not affect the growth of Itokai 1.
It was suppressed to 2 mM or less.

【0029】培養開始から6週間後、約4×106個体
/m2の密度まで培養された段階でプラスチック製容器
の内面に敷いたビニール袋を引き上げ、ビニール袋中の
海水を適宜捨てて、3〜4つのビニール袋の中身を1つ
の別のビニール袋にまとめ、汚泥浄化海域まで船を用い
て輸送した。海底へはダイバーが手で運び、汚泥上でビ
ニール袋を破って培養基質の砂ごとイトゴカイを静かに
撒布し、撒布後の海底の状況を定期的に観察した。90
日後に底層水の溶存酸素の低下が見られない健全域のレ
ベルにまで浄化されていることが確認された。
Six weeks after the start of cultivation, at the stage when the cells were cultured to a density of about 4 × 10 6 individuals / m 2 , the plastic bag laid on the inner surface of the plastic container was pulled up, and the seawater in the plastic bag was properly discarded. The contents of three to four plastic bags were combined into one separate plastic bag and transported to the sludge purification sea area by boat. Divers carried the seabed by hand, smashed plastic bags on the sludge and gently sprayed the sand with the culture substrate sand, and periodically observed the state of the seabed after the spraying. 90
It was confirmed that the water was purified to a level in a healthy region where no decrease in dissolved oxygen was observed after a day.

【0030】[0030]

【発明の効果】本発明の方法により有機物汚泥浄化用の
イトゴカイを大量に培養することができる。培養したイ
トゴカイは作業性良く有機物汚泥上に撒布することがで
き、これにより養魚場の海底に堆積している有機物汚泥
を効率的に浄化することができる。
Industrial Applicability According to the method of the present invention, it is possible to cultivate a large amount of a cocoon for purifying organic sludge. The cultured Itokai can be spread on the organic sludge with good workability, and thereby the organic sludge deposited on the seabed of the fish farm can be efficiently purified.

フロントページの続き (72)発明者 高橋 浩樹 熊本県八代市三楽町3番1号 メルシャン 株式会社八代工場内 (72)発明者 少前 圭祐 熊本県八代市三楽町3番1号 メルシャン 株式会社八代工場内 (72)発明者 徳田 貴子 熊本県八代市三楽町3番1号 メルシャン 株式会社八代工場内 Fターム(参考) 2B104 AA31 CB23 CB46 4D059 AA09 BA01 BA22 BA25 Continued on the front page (72) Inventor Hiroki Takahashi 3-1 Sanraku-cho, Yatsushiro-shi, Kumamoto Inside Mercian Co., Ltd. Yatsushiro Plant (72) Inventor Takako Tokuda 3-1 Sanraku-cho, Yatsushiro-shi, Kumamoto Merchant Yatsushiro Plant F-term (reference) 2B104 AA31 CB23 CB46 4D059 AA09 BA01 BA22 BA25

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 海水槽に収容したイトゴカイ培養基質と
イトゴカイに、餌を定期的に撒布して5〜25℃の温度
で通気しながらイトゴカイ密度4×106個体/m2以上
まで培養することを特徴とする有機物汚泥浄化用イトゴ
カイの培養方法。
The present invention relates to a method for culturing to a density of 4 × 10 6 individuals / m 2 or more while sprinkling food regularly at a temperature of 5 to 25 ° C. on a substrate and a substrate of a cultivated locust housed in a seawater tank. A method for cultivating a strawberry that purifies organic matter sludge, comprising the steps of:
【請求項2】 イトゴカイ培養基質とイトゴカイとを収
納したプラスチック製容器を海水槽の底部に載置して培
養する請求項1に記載の有機物汚泥浄化用イトゴカイの
培養方法。
2. The method for cultivating organic sludge according to claim 1, wherein a plastic container containing the substrate for cultivation of strawberry and strawberry is placed on the bottom of a seawater tank for culturing.
【請求項3】 餌を有機炭素含有量換算で1.0gC/m2
・日〜2.8gC/m2・日の量撒布する請求項1に記載の
有機物汚泥浄化用イトゴカイの培養方法。
3. The feed is 1.0 gC / m 2 in terms of organic carbon content.
· Day ~2.8gC / m 2 · day amounts spraying method for culturing organic sludge purifying Itogokai according to claim 1.
【請求項4】 海水槽のアンモニア濃度を1.2mM以下
に維持して培養する請求項1に記載の有機物汚泥浄化用
イトゴカイの培養方法。
4. The method according to claim 1, wherein the cultivation is performed while maintaining the ammonia concentration in the seawater tank at 1.2 mM or less.
【請求項5】 イトゴカイ培養基質とイトゴカイを、プ
ラスチック製容器の内面に敷いたプラスチック製シート
の上に収納して培養を行なう請求項2に記載の有機物汚
泥浄化用イトゴカイの培養方法。
5. The method according to claim 2, wherein the cultivation substrate for cultivation of organic sludge is stored by storing the substrate for cultivation and nesting on a plastic sheet laid on the inner surface of a plastic container.
【請求項6】 培養基質が細砂である請求項1または2
に記載の有機物汚泥浄化用イトゴカイの培養方法。
6. The culture substrate according to claim 1, wherein the culture substrate is fine sand.
The method for cultivating a strawberry in purifying an organic sludge according to the above item.
【請求項7】 プラスチック製容器、またはプラスチッ
ク製容器とプラスチック製シートとして、培養後のイト
ゴカイを有機物汚泥海水域に撒布する作業に耐える強度
を有するものを使用する請求項2または5に記載の有機
物汚泥浄化用イトゴカイの培養方法。
7. The organic substance according to claim 2 or 5, wherein a plastic container or a plastic container and a plastic sheet having a strength enough to withstand the operation of dispersing the cultured strawberry in an organic sludge seawater area is used. A method for cultivating a strawberry that purifies sludge.
【請求項8】 請求項1乃至7のいずれかに記載の方法
により得られたイトゴカイを高密度に含む培養基質を、
浄化対象の海水域の堆積汚泥上に撒布しイトゴカイの有
機物消費力を利用して有機物汚泥を浄化することを特徴
とする有機物汚泥の浄化方法。
8. A culture substrate containing a high density of a cod that is obtained by the method according to any one of claims 1 to 7,
A method for purifying organic matter sludge, comprising spraying on sediment sludge in a seawater area to be purified, and purifying the organic matter sludge by utilizing the organic matter consumption power of Itokai.
JP2000050762A 2000-02-28 2000-02-28 Cultivation method of organic sludge for purification of organic sludge and purification method of organic sludge Expired - Fee Related JP4049505B2 (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006121074A1 (en) * 2005-05-13 2006-11-16 Tashizen Techno Works Co., Ltd. Method of purifying water area
WO2006121075A1 (en) * 2005-05-13 2006-11-16 Keiten Co., Ltd. Method of aquafarming fishes or shellfishes
JP2007054735A (en) * 2005-08-24 2007-03-08 Kazuhiro Kogure Sludge purification method
CN104335927A (en) * 2013-07-23 2015-02-11 中国科学院海洋研究所 Cross-sea-area low carbon normal temperature spat culturing method applicable to bay scallops

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006121074A1 (en) * 2005-05-13 2006-11-16 Tashizen Techno Works Co., Ltd. Method of purifying water area
WO2006121075A1 (en) * 2005-05-13 2006-11-16 Keiten Co., Ltd. Method of aquafarming fishes or shellfishes
JP2006314954A (en) * 2005-05-13 2006-11-24 Tashizen Techno Works:Kk Water area purifying method
JP2006314281A (en) * 2005-05-13 2006-11-24 Keiten Co Ltd Method for culturing fish and shellfish
JP2007054735A (en) * 2005-08-24 2007-03-08 Kazuhiro Kogure Sludge purification method
CN104335927A (en) * 2013-07-23 2015-02-11 中国科学院海洋研究所 Cross-sea-area low carbon normal temperature spat culturing method applicable to bay scallops

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