JP5164057B2 - Culture medium for photosynthetic organisms using incinerated ash, method for producing the same, and method for culturing photosynthetic organisms - Google Patents
Culture medium for photosynthetic organisms using incinerated ash, method for producing the same, and method for culturing photosynthetic organisms Download PDFInfo
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本発明は、廃棄物である焼却灰を培地の成分として有効利用した、光合成生物を培養するための培地およびその製造方法に関するものである。さらに、光合成生物の培養方法に関するものである。 TECHNICAL FIELD The present invention relates to a medium for culturing photosynthetic organisms, which effectively uses incinerated ash, which is a waste, as a component of the medium, and a method for producing the same. Furthermore, the present invention relates to a method for culturing photosynthetic organisms.
近年、焼却灰(燃焼灰)の排出量の増加に伴い、焼却灰の処理と有効活用の技術が求められている。焼却灰は、鶏糞、豚糞および牛糞等を含む畜産系廃棄物の焼却処分、食品廃棄物、生ゴミおよび都市ゴミの焼却処分、廃材や間伐材等の林産廃棄物の焼却処分、下水処理場から排出される余剰汚泥の焼却処分、各種工場から排出される各種廃棄物の焼却処分、並びに火力発電所や燃焼炉等での石炭等の化石燃料の燃焼等によって多量に発生する。 In recent years, with the increase of incineration ash (combustion ash) emissions, technology for the treatment and effective utilization of incineration ash is required. Incineration ash is incineration of livestock waste including chicken manure, pig manure and cow manure, incineration of food waste, raw garbage and municipal waste, incineration of forest waste such as waste and thinned wood, sewage treatment plant It is generated in large quantities by incineration of surplus sludge discharged from the plant, incineration of various wastes discharged from various factories, and combustion of fossil fuels such as coal in thermal power plants and combustion furnaces.
焼却灰の処分法として先ず埋立て処理が挙げられるが、最近では埋立て処分場の確保が困難となってきており、焼却灰の減容化を図ると共に、埋立て以外の再資源化法や有効活用法の開発が強く望まれている。 Landfill treatment is one of the first disposal methods for incinerated ash, but recently it has become difficult to secure a landfill site, and in addition to reducing the volume of incinerated ash, Development of effective utilization methods is strongly desired.
これまでに、焼却灰の様々な有効利用法が検討されており、例えばセメント分野では、セメント原材料、セメント混和材およびコンクリート混和材への利用法が開発されている(特許文献1)。土木分野では、地盤改良材、道路路盤材およびアスファルト等への利用法が開発されている(特許文献2)。建築分野では、建材ボードや人工軽量骨材等への利用法が開発されている(特許文献3)。農林水産分野では、肥料や土壌改良剤等への利用法が開発されている(特許文献4)。また、焼却灰を他の無機材料やセメント等の硬化剤と混合して成型体に成型し、水に浮遊可能な藻類の培養媒体として利用する方法も開示されている(特許文献5、特許文献6)。 Various effective utilization methods of incinerated ash have been studied so far. For example, in the cement field, utilization methods for cement raw materials, cement admixtures and concrete admixtures have been developed (Patent Document 1). In the civil engineering field, utilization methods for ground improvement materials, road roadbed materials, asphalt, and the like have been developed (Patent Document 2). In the building field, a method of using a building material board, an artificial lightweight aggregate, or the like has been developed (Patent Document 3). In the field of agriculture, forestry and fisheries, utilization methods for fertilizers, soil improvers and the like have been developed (Patent Document 4). Also disclosed is a method in which incinerated ash is mixed with another inorganic material or a curing agent such as cement, molded into a molded body, and used as a culture medium for algae that can float on water (Patent Document 5, Patent Document). 6).
しかしながら、多量に発生する焼却灰の活用を図るために、これ以外の新たな分野での有効利用や有用物質の生産への利用が強く望まれていた。 However, in order to utilize the incinerated ash generated in large quantities, there has been a strong demand for effective use in other new fields and for the production of useful substances.
ところで、光合成生物である藻類は、食品分野、飼料分野および環境分野等の広い分野で現在利用されている。例えば、緑藻類のクロレラ(Chlorella)は、食品分野では、乾燥藻体が錠剤や顆粒の形態で、熱水抽出物(エキス)はドリンクの形態で健康食品として市販されている。農業分野では、クロレラエキスの植物成長剤としての利用や、乾燥藻体の肥料としての利用も行われている。水産分野では、ワムシの生産や養殖用餌料の添加剤として利用されている。 By the way, algae which are photosynthetic organisms are currently used in a wide range of fields such as food, feed and environment. For example, the green alga Chlorella is commercially available as a health food in the food field in the form of dry algae in the form of tablets and granules and hot water extract (extract) in the form of a drink. In the agricultural field, chlorella extract is also used as a plant growth agent and as a fertilizer for dry algal bodies. In the field of fisheries, it is used as an additive for rotifer production and aquaculture feed.
また、藍藻類のスピルリナ(Spirulina)は、食品分野では、栄養補助食品等の食品素材として、あるいは藻体に含まれる青色色素が食用色素として利用されている。水産分野では鑑賞魚や養殖魚の飼料添加物として、畜産分野では産卵鶏等の飼料添加物として使用されている。 In the food field, the blue-green algae Spirulina is used as a food material such as a nutritional supplement, or a blue pigment contained in an alga body as a food pigment. In the fishery field, it is used as a feed additive for appreciation fish and cultured fish, and in the livestock field, it is used as a feed additive for laying hens.
さらに最近では、地球温暖化の原因となる二酸化炭素の対策技術として、クロレラ等の藻類を光照射下で培養して、火力発電所や各種工場から排出される燃焼排ガス中の二酸化炭素を固定化させて低減し、同時に、培養した藻体の飼料への利用や、あるいは藻体からの有用物質の抽出・生産、あるいは有害化学物質の除去等、環境分野での利用も検討されている(特許文献7、特願2006−250005号を参照)。 More recently, as a measure against carbon dioxide, which causes global warming, algae such as chlorella are cultured under light irradiation to fix carbon dioxide in combustion exhaust gas discharged from thermal power plants and various factories. At the same time, the use of cultured algae for feed, the extraction and production of useful substances from algae, and the removal of hazardous chemicals is also being studied (patents) Reference 7 and Japanese Patent Application No. 2006-250005).
しかしながら、これらの光合成生物を光の照射下で人工的に培養して細胞並びに有用物質を生産する場合、培養に適した専用の培地が必要となる。培地中には、窒素、リン、カリウム、ナトリウム、マグネシウム、カルシウム、硫黄および鉄等を含む塩類、マンガン、コバルト、亜鉛およびモリブデン等の微量金属の塩類等、種々の無機栄養塩を含むことが求められるため、培地の製造には多種類の薬品が必要で調製に手間がかかり、また薬品の費用もかかってコスト高になる。 However, when these photosynthetic organisms are artificially cultured under light irradiation to produce cells and useful substances, a dedicated medium suitable for culture is required. The medium must contain various inorganic nutrient salts such as salts containing nitrogen, phosphorus, potassium, sodium, magnesium, calcium, sulfur and iron, and salts of trace metals such as manganese, cobalt, zinc and molybdenum. Therefore, the production of the culture medium requires many kinds of chemicals, and it takes time and effort to prepare them, and the cost of the chemicals is also high, resulting in high costs.
石炭灰等を水と接触させて得られる溶液に二酸化炭素を接触させたものを光合成生物の培養に用いる方法が検討されているが(特許文献7)、この方法では、石炭灰等に含まれるアルカリ金属やアルカリ土類金属等の元素は酸化物の状態で存在するため単に水と接触させるだけでは溶解量が極めて少なく、栄養成分的に不足するため、光合成生物の効率的な培養は困難であった。 A method in which carbon dioxide is brought into contact with a solution obtained by bringing coal ash or the like into contact with water has been studied (Patent Document 7), but this method includes coal ash and the like. Since elements such as alkali metals and alkaline earth metals exist in the form of oxides, the amount of dissolution is extremely small by simply contacting with water, and there is a lack of nutritional components, making it difficult to efficiently cultivate photosynthetic organisms. there were.
そこで、簡便でかつ安価に調製でき、効率よく大量に光合成生物を培養できる経済的な培地の開発と、その培地の光合成生物の生産および有用物質の生産への利用が強く望まれていた。 Therefore, there has been a strong demand for the development of an economical medium that can be easily and inexpensively prepared and that can efficiently cultivate a large amount of photosynthetic organisms, and that the medium can be used for production of photosynthetic organisms and production of useful substances.
本発明は、廃棄物である焼却灰の有効利用を図り、光合成生物の培養に利用可能な培地を簡便かつ安価に提供することを課題とする。また、焼却灰を利用した光合成生物の培養方法を提供することを課題とする。 An object of the present invention is to effectively use the incinerated ash that is a waste and to provide a medium that can be used for culturing photosynthetic organisms simply and inexpensively. Another object of the present invention is to provide a method for culturing photosynthetic organisms using incinerated ash.
本発明者らは、かかる課題を解決すべく鋭意研究の結果、焼却灰を酸で溶解して得られる溶液が藻類等の光合成生物を培養するための培地として利用できることを見出し、本発明を完成するに至った。 As a result of earnest research to solve such problems, the present inventors have found that a solution obtained by dissolving incinerated ash with an acid can be used as a medium for culturing photosynthetic organisms such as algae, and completed the present invention. It came to do.
すなわち本発明の要旨は以下の通りである。
(1)焼却灰を酸で溶解して調製される溶液を含む光合成生物の培養培地。
(2)前記酸が、硝酸、硫酸および塩酸から選ばれる一以上である上記(1)に記載の光合成生物の培養培地。
(3)前記焼却灰が、鶏糞の焼却灰である上記(1)又は(2)に記載の光合成生物の培養培地。
(4)前記溶液に、鉄塩もしくは銅塩またはその両方をさらに添加してなる上記(1)〜(3)のいずれかに記載の光合成生物の培養培地。
(5)焼却灰を酸で溶解させ、得られた溶液を用いて光合成生物を培養する、光合成生物の培養方法。
(6)焼却灰を酸で溶解して溶液を調製し、該溶液を含む培養培地を製造する光合成生物の培養培地の製造方法。
That is, the gist of the present invention is as follows.
(1) A culture medium for photosynthetic organisms containing a solution prepared by dissolving incinerated ash with an acid.
(2) The culture medium for photosynthetic organisms according to (1) above, wherein the acid is one or more selected from nitric acid, sulfuric acid and hydrochloric acid.
(3) The culture medium for photosynthetic organisms according to (1) or (2) above, wherein the incineration ash is incineration ash of chicken dung.
(4) The culture medium for photosynthetic organisms according to any one of (1) to (3) above, wherein an iron salt or a copper salt or both are further added to the solution.
(5) A method for cultivating photosynthetic organisms, wherein incinerated ash is dissolved with an acid, and the photosynthetic organism is cultured using the obtained solution.
(6) A method for producing a culture medium for photosynthetic organisms, which comprises preparing a solution by dissolving incinerated ash with an acid and producing a culture medium containing the solution.
本発明の培養培地は、藻類等の光合成生物を培養するための培地として利用できる。培地を調製する際に廃棄物である焼却灰を原料に用いるため、簡便かつ安価に光合成生物の培養と有用物質の生産を行うことができる。また焼却灰を培養培地の成分として利用することで、産業廃棄物である焼却灰の有効活用と再利用を図ることができる。 The culture medium of the present invention can be used as a medium for culturing photosynthetic organisms such as algae. Since incinerated ash, which is a waste, is used as a raw material when preparing the medium, it is possible to culture photosynthetic organisms and produce useful substances easily and inexpensively. Moreover, by using the incineration ash as a component of the culture medium, it is possible to effectively use and reuse the incineration ash that is industrial waste.
以下、本発明を詳細に説明する。
本発明で使用される焼却灰としては、鶏糞、豚糞および牛糞等の畜産廃棄物、生ゴミ、都市ゴミ、食品廃棄物、廃材や間伐材等の林産廃棄物、下水処理場汚泥、工場から排出される廃棄物等の、各種の有機性廃棄物を燃焼した際に排出される灰や、火力発電所や燃焼炉等で石炭等の固形燃料を燃焼した際に排出される灰等を用いることができる。
Hereinafter, the present invention will be described in detail.
Incinerated ash used in the present invention includes livestock waste such as chicken dung, pig dung and cow dung, raw garbage, municipal waste, food waste, forest waste such as waste and thinned wood, sewage treatment plant sludge, and factory Use ash discharged when burning various organic waste such as discharged waste, or ash discharged when burning solid fuel such as coal in a thermal power plant or combustion furnace, etc. be able to.
その中でも、鶏糞の燃焼により排出される灰(鶏糞焼却灰)は特に好ましく用いられる。鶏糞焼却灰は、燃焼条件等によって組成は異なるが、約25〜約55重量%のCaO、約7〜約25重量%のK2O、約9〜約15重量%のP2O5、約3〜約12重量%のSO3、約1〜約7重量%のCl、約2〜約3重量%のMgO、1未満〜約3重量%のNa2O、および約1〜約4重量%のSiO2等を含み、ナトリウム、カリウム、カルシウム、マグネシウム、リン等の有用な元素から構成されるため、光合成生物の培養培地の原料として好適である。 Among these, ash (chicken manure incineration ash) discharged by the combustion of chicken manure is particularly preferably used. The composition of incinerated chicken manure ash varies depending on the combustion conditions, etc., but is about 25 to about 55 wt% CaO, about 7 to about 25 wt% K 2 O, about 9 to about 15 wt% P 2 O 5 , about 3 to about 12 wt% of SO 3, from about 1 to about 7 weight percent of Cl, from about 2 to about 3 wt% of MgO, 1 to less than about 3 wt% of Na 2 O, and from about 1 to about 4 wt% by weight of SiO 2 or the like, since the sodium, potassium, calcium, magnesium, is composed of useful elements such as phosphorus, it is suitable as a raw material for culture medium photosynthetic organisms.
焼却灰を溶解する酸としては、鉱酸、有機酸、炭酸等の種々の酸を挙げることができ、中でも硝酸、硫酸、塩酸等の鉱酸が好適に用いられる。これらの硝酸、硫酸および鉱酸は、いずれか1種類のみを用いても良く、あるいは2種もしくは3種類全てを組み合わせて用いても良い。硝酸中の硝酸イオンは、藻類等の光合成生物の生育に必要な窒素源として利用できるため、少なくとも硝酸を成分に含むことが好ましく、最も好ましくは硝酸、硫酸および塩酸の3つの酸を組み合わせた混合酸である。混合酸を用いる場合、各成分の混合比は、焼却灰や培養する光合成生物の種類等を考慮して適宜設定することができる。一般的には、体積比で硝酸を100としたとき、同モル濃度の硫酸が5〜20、塩酸が10〜30程度である。 Examples of the acid that dissolves the incinerated ash include various acids such as mineral acids, organic acids, and carbonic acids. Among these, mineral acids such as nitric acid, sulfuric acid, and hydrochloric acid are preferably used. Any one of these nitric acid, sulfuric acid, and mineral acid may be used, or two or all three types may be used in combination. Since nitrate ions in nitric acid can be used as a nitrogen source necessary for the growth of photosynthetic organisms such as algae, it is preferable to contain at least nitric acid as a component, and most preferably a mixture of three acids of nitric acid, sulfuric acid and hydrochloric acid. It is an acid. In the case of using a mixed acid, the mixing ratio of each component can be appropriately set in consideration of incineration ash, the type of photosynthetic organism to be cultured, and the like. Generally, when nitric acid is 100 by volume ratio, sulfuric acid with the same molarity is about 5 to 20, and hydrochloric acid is about 10 to 30.
これらの酸に焼却灰を添加して攪拌等により溶解させ、その後遠心分離、ろ過等の手段により未溶解の焼却灰を分離し、得られた溶液のpHを培養する光合成生物の培養に適するpHに調整し、さらに必要に応じ水で希釈する等して培養する光合成生物の培養に適する培地濃度に調節することで、本発明の培養培地が得られる。このような焼却灰の溶液を含む培養培地中には、焼却灰に存在するナトリウム、カリウム、カルシウム、マグネシウム、鉄、リン等の各種元素が塩の状態で溶解しており、藻類等の光合成生物が光合成独立栄養条件下で生育する際の栄養塩として利用することができる。 A pH suitable for cultivation of photosynthetic organisms in which incinerated ash is added to these acids and dissolved by stirring or the like, and then undissolved incinerated ash is separated by means of centrifugation, filtration, etc., and the pH of the resulting solution is cultured. The culture medium of the present invention is obtained by adjusting to a medium concentration suitable for culturing photosynthetic organisms to be cultured by, for example, diluting with water if necessary. In the culture medium containing such incinerated ash solution, various elements such as sodium, potassium, calcium, magnesium, iron, and phosphorus present in the incinerated ash are dissolved in a salt state, and photosynthetic organisms such as algae are dissolved. Can be used as a nutrient when growing under photoautotrophic conditions.
なお、本発明の培養培地は、上記のように溶液の状態で用いることができるが、その他の方法として溶液を寒天等とともに溶解・固化させ、固体培地もしくは半流動培地としても良い。 The culture medium of the present invention can be used in the state of a solution as described above. Alternatively, the solution may be dissolved and solidified with agar or the like to form a solid medium or a semi-fluid medium.
さらに本発明の培養培地には、必要に応じて、各種の塩を添加することができる。これにより光合成生物に必要な栄養分を補うことができる。具体的な塩の種類としては、FeSO4・7H2O等の鉄塩、CuSO4・5H2O等の銅塩、および鉄塩と銅塩の組み合わせ等を挙げることができる。また、硝酸塩は、特に焼却灰を溶解させる酸がH2SO4とHClのみで構成される混合酸である場合、窒素源として利用できるため好ましく添加される。 Furthermore, various salts can be added to the culture medium of the present invention as necessary. This makes it possible to supplement the nutrients necessary for the photosynthetic organism. Specific examples of the salt include iron salts such as FeSO 4 · 7H 2 O, copper salts such as CuSO 4 · 5H 2 O, and combinations of iron salts and copper salts. Nitrate is preferably added because it can be used as a nitrogen source, particularly when the acid that dissolves the incinerated ash is a mixed acid composed of only H 2 SO 4 and HCl.
塩の添加量は、焼却灰の種類等によって異なり、特に限定されるものではないが、例えば鶏糞焼却灰を原料とする培地については、水で希釈する等して適切なpHに調製した後の培地に対し、鉄塩がFe換算で約0.1〜約2mg/L、銅塩がCu換算で約0.01〜約0.03mg/Lとすることが好ましく、硝酸塩を加える場合は約200〜約2500mg/L程度の添加量とすることが好ましい。 The amount of salt to be added varies depending on the type of incineration ash and the like, and is not particularly limited. For example, for a medium using chicken manure incineration ash as a raw material, the medium is diluted with water and adjusted to an appropriate pH. Preferably, the iron salt is about 0.1 to about 2 mg / L in terms of Fe and the copper salt is about 0.01 to about 0.03 mg / L in terms of Cu with respect to the medium. It is preferable to set the addition amount to about 2500 mg / L.
以上のような焼却灰から調製された溶液を含む培地で培養できる光合成生物としては、例えば、緑藻類であるクロレラ属、藍藻類であるスピルリナ属等が挙げられるが、これらの藻類に限られたものではなく、その他の藻類、植物プランクトン、海藻、海草、光合成細菌、野菜等の各種植物など、光合成独立栄養的に生育するものであればどのような光合成生物も培養可能である。なお、光合成生物は、本発明の培養培地に直接播種しても良く、あるいは藻類用培地であるMBM培地等の通常の培地で予め光合成生物の培養を行って前培養液を得、その前培養液を本発明の培養培地に加えても良い。また、焼却灰の溶液自体を培養培地として利用する場合のみならず、例えば焼却灰の溶液を野菜等の養液栽培(水耕栽培等)における培養液(液体肥料)として用いることもできる。 Examples of photosynthetic organisms that can be cultured in a medium containing a solution prepared from incinerated ash as described above include the genus Chlorella, which is a green alga, and the genus Spirulina, which is a cyanobacteria. Instead, any photosynthetic organism can be cultured as long as it grows photoautotrophically, such as other plants such as algae, phytoplankton, seaweed, seaweed, photosynthetic bacteria, and vegetables. The photosynthetic organisms may be directly seeded in the culture medium of the present invention, or a precultured solution is obtained by previously culturing the photosynthetic organisms in a normal medium such as an algae medium such as MBM medium. The liquid may be added to the culture medium of the present invention. In addition, when the incinerated ash solution itself is used as a culture medium, for example, the incinerated ash solution can be used as a culture liquid (liquid fertilizer) in hydroponic culture (hydroponic culture etc.) such as vegetables.
さらに、藻類等の光合成生物が光照射下で光合成独立栄養的に生育する際には炭素源が必要であるが、この炭素源を確保するため、例えば培養培地を設置した容器を振盪することで大気中の二酸化炭素を培地中に溶解させ、これを炭素源として利用することができる。また、焼却灰を溶解させた溶液への炭酸水素ナトリウムの添加、あるいは空気や二酸化炭素を含有するガスの培養容器内への通気により、培地中に溶解する炭酸イオンの濃度が増大し、それによって光合成生物の生育速度と増殖量を向上させることができる。 Furthermore, when photosynthetic organisms such as algae grow photoautotrophically under light irradiation, a carbon source is required. To secure this carbon source, for example, by shaking a container in which a culture medium is installed. Carbon dioxide in the atmosphere can be dissolved in the medium and used as a carbon source. In addition, the concentration of carbonate ions dissolved in the medium is increased by the addition of sodium hydrogen carbonate to the solution in which the incinerated ash is dissolved, or by aeration of gas containing air or carbon dioxide into the culture vessel. The growth rate and growth amount of photosynthetic organisms can be improved.
以下、実施例を挙げて、本発明を詳細に説明するが、本発明がこれら実施例のみに限定されないことは言うまでもない。 EXAMPLES Hereinafter, although an Example is given and this invention is demonstrated in detail, it cannot be overemphasized that this invention is not limited only to these Examples.
以下の各実施例および参考例では、光合成生物の緑藻類であるクロレラ属の株として、国立大学法人東京大学のIAMカルチャーコレクションから入手したクロレラブルガリス(Chlorella vulgaris)IAM C−27、クロレラソロキニアナ(Chlorella sorokiniana)IAM C−212、クロレラケスレリ(Chlorella kessleri)IAM C−531、クロレラブルガリス(Chlorella vulgaris)IAM C−536、クロレラブルガリス(Chlorella vulgaris)IAM C−547およびクロレラ(Chlorella sp.)IAM C−628、研究室で分離・保存しているクロレラブルガリス(Chlorella vulgaris)MKJ−34(特願2006−250005号)およびクロレラブルガリス(Chlorella vulgaris)C−1(特願2006−250005号)を使用した。 In the following Examples and Reference Examples, Chlorella vulgaris IAM C-27, Chlorella solokiniana obtained from the IAM Culture Collection of the University of Tokyo as a strain of the genus Chlorella, a green alga of a photosynthetic organism, (Chlorella sorokiniana) IAM C-212, Chlorella kessleri IAM C-531, Chlorella vulgaris IAM C-536, Chlorella vulgar I (Clorella vulgarh) ) IAM C-628, Chlorella vulgar separated and stored in the laboratory s) MKJ-34 (Japanese Patent Application No. 2006-250005) and Chlorella vulgaris (Chlorella vulgaris) were used C-1 (Japanese Patent Application No. 2006-250005).
また、藍藻類であるスピルリナ属の株として、独立行政法人国立環境研究所から入手したスピルリナプラテンシス(Spirulina platensis)NIES−39、スピルリナプラテンシス(Spirulina platensis)NIES−45、スピルリナプラテンシス(Spirulina platensis)NIES−46およびスピルリナプラテンシス(Spirulina platensis)NIES−597を用いた。 Furthermore, as a strain of the genus Spirulina, which is a cyanobacteria, Spirulina platensis NIES-39, Spirulina platensis NIES-45, Spirulina platensis (Spirulina platensis) obtained from the National Institute for Environmental Studies. ) NIES-46 and Spirulina platensis NIES-597 were used.
クロレラ属の前培養には、表1、表2および表3で示されるMBM培地を用い、蛍光灯での光照射下(5500Lux、12時間暗−12時間明)、30℃の条件下で6日間の静置培養を行って前培養液を得た。 For the pre-culture of the genus Chlorella, the MBM medium shown in Table 1, Table 2 and Table 3 was used, and under the light irradiation with a fluorescent lamp (5500 Lux, 12 hours dark-12 hours light) under the conditions of 30 ° C. A pre-culture solution was obtained by stationary culture for one day.
スピルリナ属の前培養には、表4および表5に示すSOT培地またはMA培地を用い、蛍光灯での光照射下(5500Lux、12時間暗−12時間明)、30℃の条件下で6日間の静置培養を行って前培養液を得た。 For the preculture of Spirulina, the SOT medium or MA medium shown in Tables 4 and 5 was used, and the light was irradiated with a fluorescent lamp (5500 Lux, 12 hours dark-12 hours light) at 30 ° C. for 6 days. Was subjected to stationary culture to obtain a preculture solution.
(実施例1、参考例1)
焼却灰を用いた培養培地を以下のようにして調製した。0.1mol/LのHNO3、0.1mol/LのH2SO4および0.1mol/LのHClを体積比で25:3:5の比率で混ぜた混合酸50mlをビーカーに入れ、マグネチックスターラーで撹拌しながら鶏糞焼却灰を少量ずつ添加し、溶液のpHが5.4になるまで鶏糞焼却灰を溶解させた。酸による溶解処理により、鶏糞焼却灰は元の重量の約60%相当分が溶解し、焼却灰の減容化を行うことができた。焼却灰を溶解した溶液を遠心分離(10,000rpm、10分間)して未溶解の焼却灰を取り除き、得られた上澄み液を蒸留水で30倍に希釈したものを培養培地として用いた。
(Example 1, Reference Example 1)
A culture medium using incinerated ash was prepared as follows. 50 ml of a mixed acid prepared by mixing 0.1 mol / L HNO 3 , 0.1 mol / L H 2 SO 4 and 0.1 mol / L HCl at a volume ratio of 25: 3: 5 was put in a beaker, While stirring with a tic stirrer, chicken manure incineration ash was added little by little to dissolve the chicken manure incineration ash until the pH of the solution reached 5.4. Due to the dissolution treatment with acid, the equivalent of about 60% of the original weight of the chicken manure incineration ash was dissolved, and the volume of the incineration ash was reduced. A solution in which the incinerated ash was dissolved was centrifuged (10,000 rpm, 10 minutes) to remove undissolved incinerated ash, and a supernatant obtained by diluting 30 times with distilled water was used as a culture medium.
次に、上記のように鶏糞焼却灰を用いて調製した培養培地をL字型試験管に10mL添加し、オートクレーブ(121℃、15分間)で滅菌した。滅菌後、上記各種のクロレラ属の藻体の前培養液0.3mLを接種し、培養温度30℃、蛍光灯での光照射(5500Lux、12時間暗−12時間明)の条件下で7日間の振盪培養を行った。培養開始時と培養終了時の培養液について、紫外可視分光光度計(島津製作所UVmini−1240)を用いて波長660nmでの吸光度(OD660)を測定し、その吸光度(OD660)の差から生育度を求めた。 Next, 10 mL of the culture medium prepared using chicken manure incineration ash as described above was added to an L-shaped test tube, and sterilized by autoclaving (121 ° C., 15 minutes). After sterilization, inoculate 0.3 mL of the pre-culture solution of the above-mentioned various chlorella algae, and culture for 7 days under conditions of 30 ° C. and irradiation with fluorescent light (5500 Lux, 12 hours dark-12 hours light) Were subjected to shaking culture. The culture solution at the end of the culture and at the initiation of the culture, using ultraviolet-visible spectrophotometer (Shimadzu UVmini-1240) was measured and the absorbance (OD 660) at a wavelength of 660 nm, growing from the difference of the absorbance (OD 660) I asked for a degree.
また、クロレラ属の培養に使用されるMBM培地でも同様の方法で培養して生育度を求め(参考例1)、本発明による培養培地での生育度と比較した。この測定結果を図1に示す。 Further, the MBM medium used for culturing Chlorella was also cultured in the same manner to determine the degree of growth (Reference Example 1), and compared with the degree of growth in the culture medium according to the present invention. The measurement results are shown in FIG.
図1に示すように、鶏糞焼却灰を用いた本発明の培地で培養すると、クロレラ属の種類によって生育度は異なるものの、MBM培地で培養したときとほぼ同程度の生育が得られ、したがって本発明による培養培地がクロレラ属の培地として利用できることが分かった。 As shown in FIG. 1, when cultured on the medium of the present invention using chicken manure incineration ash, although the degree of growth varies depending on the type of genus Chlorella, growth similar to that obtained when cultured on MBM medium is obtained. It has been found that the culture medium according to the invention can be used as a medium for Chlorella.
(実施例2、参考例2)
上記実施例1における鶏糞焼却灰を用いて調製した焼却灰培地をL字型試験管に10mL添加し、オートクレーブ(121℃、15分間)で滅菌した。滅菌後、各種のスピルリナ属の藻体の前培養液0.3mLを接種し、培養温度30℃、蛍光灯での光照射(5500Lux、12時間暗−12時間明)の条件下で7日間の振盪培養を行った。培養開始時と培養終了時の培養液の吸光度(OD660)の差から生育度を求めた。また、スピルリナ属の培養に使用されるSOT培地またはMA培地でも同様の方法で培養して生育度を求め(参考例2および3)、本発明による培養培地での生育度と比較した。この測定結果を図2に示す。
(Example 2, Reference Example 2)
10 mL of the incineration ash medium prepared using the chicken manure incineration ash in Example 1 was added to an L-shaped test tube, and sterilized by autoclaving (121 ° C., 15 minutes). After sterilization, inoculate 0.3 mL of a preculture of various Spirulina alga bodies for 7 days under conditions of culture temperature 30 ° C. and irradiation with fluorescent light (5500 Lux, 12 hours dark-12 hours light). Shaking culture was performed. The degree of growth was determined from the difference in absorbance (OD 660 ) of the culture solution at the start of culture and at the end of culture. In addition, the SOT medium or MA medium used for culturing Spirulina was cultured in the same manner to determine the degree of growth (Reference Examples 2 and 3), and compared with the degree of growth in the culture medium according to the present invention. The measurement results are shown in FIG.
図2に示すように、鶏糞焼却灰を用いた培地で培養すると、スピルリナ属の株の違いによって生育度は異なるものの、SOT培地またはMA培地で培養したときとほぼ同程度の生育が得られ、したがって本発明による培養培地がスピルリナ属の培地として利用できることが分かった。 As shown in FIG. 2, when cultured in a medium using chicken manure incineration ash, the degree of growth varies depending on the strain of the genus Spirulina, but almost the same growth as when cultured in the SOT medium or MA medium is obtained. Therefore, it has been found that the culture medium according to the present invention can be used as a Spirulina medium.
(実施例3〜6)
培養培地を調製する際に、混合酸の組成を変えて焼却灰を溶解させ、得られた培養培地での生育度を検討した。具体的には、0.1mol/LのHNO3、0.1mol/LのH2SO4および0.1mol/LのHClを、25:3:5(実施例3)、25:3:0(実施例4)、25:0:5(実施例5)、0:3:5(実施例6)、の体積比で混ぜた4種類の混合酸を用いた。4種類の混合酸50mLをそれぞれビーカーに入れ、マグネチックスターラーで撹拌しながら鶏糞焼却灰を少量ずつ添加し、溶液のpHが5.4になるまで鶏糞焼却灰を溶解させた。鶏糞焼却灰が溶解した溶液を遠心分離(10,000rpm、10分間)して未溶解の焼却灰を取り除き、得られた4種類の上澄み液を蒸留水で30倍に希釈したものを培地として用いた。
(Examples 3 to 6)
When preparing the culture medium, the composition of the mixed acid was changed to dissolve the incinerated ash, and the degree of growth in the obtained culture medium was examined. Specifically, 0.1 mol / L HNO 3 , 0.1 mol / L H 2 SO 4 and 0.1 mol / L HCl were added at 25: 3: 5 (Example 3), 25: 3: 0. (Example 4), four mixed acids mixed at a volume ratio of 25: 0: 5 (Example 5) and 0: 3: 5 (Example 6) were used. Four kinds of mixed acids (50 mL) were put in a beaker, and chicken dung incineration ash was added little by little while stirring with a magnetic stirrer. The chicken dung incineration ash was dissolved until the pH of the solution reached 5.4. Centrifugation (10,000 rpm, 10 minutes) of the solution in which chicken manure incineration ash was dissolved to remove undissolved incineration ash, and the resulting four types of supernatants diluted 30 times with distilled water were used as the medium. It was.
4種類の培養培地をL字型試験管に10mL添加し、オートクレーブ(121℃、15分間)で滅菌した。滅菌後、クロレラブルガリス(Chlorella vulgaris)MKJ−34およびクロレラブルガリス(Chlorella vulgaris)C−1の前培養液0.3mlを接種し、培養温度30℃、蛍光灯での光照射(5500Lux、12時間暗−12時間明)の条件下で7日間の振盪培養を行った。培養開始時と培養終了時の培養液の吸光度(OD660)の差から生育度を求めた。この測定結果を表6に示す。 Four types of culture media were added to an L-shaped test tube in an amount of 10 mL, and sterilized by autoclaving (121 ° C., 15 minutes). After sterilization, 0.3 ml of the preculture of Chlorella vulgaris MKJ-34 and Chlorella vulgaris C-1 was inoculated, and the light was irradiated with fluorescent light (5500 Lux, 12 Shaking culture was performed for 7 days under the conditions of time dark-12 hours light. The degree of growth was determined from the difference in absorbance (OD 660 ) of the culture solution at the start of culture and at the end of culture. The measurement results are shown in Table 6.
表6に示すように、HNO3、H2SO4およびHClのうち2種を含む酸で調製した実施例3〜6の培養培地は、いずれもクロレラ属の培地として利用可能であることが明らかとなった。その中でも、HNO3、H2SO4およびHClの3種類の酸を全て含む混合酸で調製した培養培地において、両方のクロレラとも生育度が最も高いことが分かった。また、H2SO4とHClだけで構成される混合酸で調製した培養培地では生育度が若干低かった。これは、HNO3を含まないために培地中の窒素源が少ないことが原因と考えられる。従って、培養培地を調製する際には、焼却灰を溶解する混合酸としてHNO3、H2SO4およびHClの3者を含有する方が好ましく、特にHNO3を含有させることが好ましいことが分かった。 As shown in Table 6, it is clear that any of the culture media of Examples 3 to 6 prepared with an acid containing two kinds of HNO 3 , H 2 SO 4 and HCl can be used as a Chlorella genus medium. It became. Among them, in the culture medium prepared with a mixed acid containing all three types of acids HNO 3 , H 2 SO 4 and HCl, both chlorella were found to have the highest growth. In addition, the growth degree of the culture medium prepared with a mixed acid composed of only H 2 SO 4 and HCl was slightly low. This is considered to be because there is little nitrogen source in the culture medium because it does not contain HNO 3 . Therefore, when preparing the culture medium, it is preferable to contain three of HNO 3 , H 2 SO 4 and HCl as the mixed acid for dissolving the incineration ash, and it is particularly preferable to contain HNO 3. It was.
(実施例7〜14)
培養培地の調製において、0.1mol/LのHNO3、0.1mol/LのH2SO4および0.1mol/LのHClを体積比で25:3:5の比率で混ぜた混合酸を用いて、鶏糞焼却灰(実施例7)または豚糞と木炭の混合物を燃焼して得られる豚糞・木炭焼却灰(実施例8)を溶解して得られた溶液を30倍希釈したものを培養培地として用いた。これらの培養培地をL字型試験管に10mL添加し、オートクレーブ(121℃、15分間)で滅菌した後、クロレラブルガリス(Chlorella vulgaris)MKJ−34の前培養液0.3mlを接種し、培養温度30℃、蛍光灯での光照射(5500Lux、12時間暗−12時間明)の条件下で7日間の振盪培養を行った。培養開始時と培養終了時の培養液の吸光度(OD660)の差から生育度を求めた。
(Examples 7 to 14)
In the preparation of the culture medium, a mixed acid prepared by mixing 0.1 mol / L HNO 3 , 0.1 mol / L H 2 SO 4 and 0.1 mol / L HCl at a volume ratio of 25: 3: 5 was used. Use a 30-fold diluted solution obtained by dissolving pig dung incineration ash (Example 7) or swine dung and charcoal incineration ash (Example 8) obtained by burning a mixture of pig dung and charcoal Used as culture medium. After adding 10 mL of these culture media to an L-shaped test tube and sterilizing with an autoclave (121 ° C., 15 minutes), inoculated with 0.3 ml of a pre-culture solution of Chlorella vulgaris (Klorella vulgaris) MKJ-34 and cultured. The shaking culture was performed for 7 days under the conditions of a temperature of 30 ° C. and light irradiation with a fluorescent lamp (5500 Lux, 12 hours dark—12 hours light). The degree of growth was determined from the difference in absorbance (OD 660 ) of the culture solution at the start of culture and at the end of culture.
また、上記のように鶏糞焼却灰から調製した培養培地に対し、さらにFeSO4・7H2Oを2mg/Lの濃度となるように添加した培地(実施例9)、CuSO4・5H2Oを0.079mg/Lの濃度となるように添加した培地(実施例10)、並びにFeSO4・7H2OおよびCuSO4・5H2Oを各々2mg/Lおよび0.079mg/Lの濃度となるように添加した培地(実施例11)を調製し、同様の方法で振盪培養を行い、生育度を求めた。 Further, to the culture medium prepared from chicken manure incineration ash as described above, a medium (Example 9) in which FeSO 4 · 7H 2 O was further added to a concentration of 2 mg / L, CuSO 4 · 5H 2 O was added. Medium added to a concentration of 0.079 mg / L (Example 10), and FeSO 4 · 7H 2 O and CuSO 4 · 5H 2 O to a concentration of 2 mg / L and 0.079 mg / L, respectively. The culture medium added to (Example 11) was prepared, shake culture was performed in the same manner, and the degree of growth was determined.
さらに、豚糞・木炭焼却灰から調製した培養培地に対しても、FeSO4・7H2Oを2mg/Lの濃度となるように添加した培地(実施例12)、CuSO4・5H2Oを0.079mg/Lの濃度となるように添加した培地(実施例13)、並びにFeSO4・7H2OおよびCuSO4・5H2Oを各々2mg/Lおよび0.079mg/Lの濃度となるように添加した培地(実施例14)を調製し、振盪培養を行って生育度を求めた。 Furthermore, a culture medium prepared from pig excrement / charcoal incineration ash with FeSO 4 · 7H 2 O added to a concentration of 2 mg / L (Example 12), CuSO 4 · 5H 2 O Medium added to a concentration of 0.079 mg / L (Example 13), and FeSO 4 · 7H 2 O and CuSO 4 · 5H 2 O to a concentration of 2 mg / L and 0.079 mg / L, respectively. A medium (Example 14) added to was prepared and shake-cultured to determine the degree of growth.
以上の測定結果を図3に示す。
図3に示すように、豚糞・木炭焼却灰から調製した培養培地でもクロレラのような光合成生物を培養するための培地として利用できることが分かった。また、鶏糞焼却灰および豚糞・木炭焼却灰を用いて調製した培養培地では、微量の鉄塩と銅塩を添加すると、無添加の場合に比べて生育度が高くなる傾向を示した。
The above measurement results are shown in FIG.
As shown in FIG. 3, it was found that even a culture medium prepared from swine dung and charcoal incinerated ash can be used as a medium for culturing a photosynthetic organism such as chlorella. Moreover, in the culture medium prepared using chicken manure incineration ash and pig manure / charcoal incineration ash, the addition of a small amount of iron salt and copper salt tended to increase the growth rate compared to the case of no addition.
(実施例15)
0.1mol/LのHNO3、0.1mol/LのH2SO4および0.1mol/LのHClを体積比が25:3:5になるように混ぜた混合酸を用いて、鶏糞焼却灰を溶解して得られた30倍希釈の培養培地280mLを300mLの三角フラスコに添加し、オートクレーブ(121℃、15分間)で滅菌した。滅菌後、クロレラブルガリス(Chlorella vulgaris)MKJ−34の前培養液20mLを添加し、CO2濃度が5%となるように空気にCO2ガスを混ぜた混合ガス(CO25%,空気95%)を300mL/minの流量で通気しながら、培養温度30℃、蛍光灯での光照射(5500Lux、12時間暗−12時間明)の条件下で7日間通気培養を行い、培養開始時と培養終了時の培養液の吸光度(OD660)の差から生育度を求めた。
(Example 15)
Incinerating chicken manure using mixed acid prepared by mixing 0.1 mol / L HNO 3 , 0.1 mol / L H 2 SO 4 and 0.1 mol / L HCl to a volume ratio of 25: 3: 5 280 mL of 30-fold diluted culture medium obtained by dissolving ash was added to a 300 mL Erlenmeyer flask and sterilized by autoclaving (121 ° C., 15 minutes). After sterilization, 20 mL of a pre-culture solution of Chlorella vulgaris MKJ-34 was added, and a mixed gas (CO 2 5%, air 95) in which CO 2 gas was mixed with air so that the CO 2 concentration was 5%. %) And aeration at a flow rate of 300 mL / min, aeration culture is performed for 7 days under the conditions of a culture temperature of 30 ° C. and light irradiation with a fluorescent lamp (5500 Lux, 12 hours dark—12 hours light). The degree of growth was determined from the difference in absorbance (OD 660 ) of the culture solution at the end of the culture.
(実施例16)
また、実施例15における培養培地に対し、FeSO4・7H2OおよびCuSO4・5H2Oが各々2mg/Lおよび0.079mg/Lの濃度となるように添加した。この鉄塩と銅塩を添加した培養培地280mLを300mLの三角フラスコに入れ、オートクレーブ(121℃、15分間)で滅菌した後、実施例15と同様の方法でクロレラブルガリス(Chlorella vulgaris)MKJ−34の通気培養を行い、培養開始時と培養終了時の培養液の吸光度(OD660)の差から生育度を求めた。
(Example 16)
Further, FeSO 4 · 7H 2 O and CuSO 4 · 5H 2 O were added to the culture medium in Example 15 so as to have concentrations of 2 mg / L and 0.079 mg / L, respectively. After 280 mL of the culture medium added with the iron salt and copper salt was placed in a 300 mL Erlenmeyer flask and sterilized by autoclaving (121 ° C., 15 minutes), Chlorella vulgaris (Klorella vulgaris) MKJ- 34 aeration cultures were performed, and the degree of growth was determined from the difference in the absorbance (OD 660 ) of the culture solution at the start and end of the culture.
(参考例4)
さらに、実施例15および16の培養培地での通気培養と比較するために、MBM培地280mLを300mLの三角フラスコに入れ、オートクレーブ(121℃、15分間)で滅菌した後、実施例15と同様の方法でクロレラブルガリス(Chlorella vulgaris)MKJ−34の通気培養を行い、培養開始時と培養終了時の培養液の吸光度(OD660)の差から生育度を求めた。
実施例15および16、並びに参考例4の測定結果を、表7に示す。
(Reference Example 4)
Furthermore, in order to compare with aeration culture in the culture medium of Examples 15 and 16, 280 mL of MBM medium was put into a 300 mL Erlenmeyer flask and sterilized by autoclave (121 ° C., 15 minutes), and then the same as in Example 15 Using the method, Chlorella vulgaris (Klorella vulgaris) MKJ-34 was aerated and the degree of growth was determined from the difference in absorbance (OD 660 ) of the culture solution at the start and end of the culture.
The measurement results of Examples 15 and 16 and Reference Example 4 are shown in Table 7.
表7に示すように、図1での振盪培養と同様に、焼却灰から調製した培地での通気培養でもクロレラの培養が可能であることが分かった。ここで、MBM培地での通気培養の結果と比べると、実施例15における通気培養の生育度が若干低いが、培地に微量のFeSO4・7H2OとCuSO4・5H2Oを添加した実施例16における通気培養ではMBM培地のものよりも高い生育度が得られることが分かった。従って、本発明による培地は通気培養下での光合成生物の培養にも適しており、原料となる焼却灰の種類によっては、適当な塩類を微量補充することでさらに生育度を向上することが可能である。 As shown in Table 7, it was found that chlorella can be cultured by aeration culture using a medium prepared from incinerated ash, as in the case of shaking culture in FIG. Here, compared with the result of the aeration culture in the MBM medium, the growth degree of the aeration culture in Example 15 was slightly low, but the trace amounts of FeSO 4 · 7H 2 O and CuSO 4 · 5H 2 O were added to the culture medium. It was found that the aeration culture in Example 16 gave a higher degree of growth than that of the MBM medium. Therefore, the medium according to the present invention is also suitable for culturing photosynthetic organisms under aeration culture, and depending on the type of incinerated ash used as a raw material, the growth degree can be further improved by supplementing with a small amount of appropriate salts. It is.
以上説明してきたように、本発明によれば、焼却灰を酸によって溶解して得られる溶液は藻類等の光合成生物の生育に必要な栄養分を含有していることから培地として使用することができる。また、本発明の培養培地は、光照射下での振盪培養や通気培養等により藻類等の光合成生物を培養できることから、クロレラやスピルリナをはじめとする各種の光合成生物の培養と生物体の生産、並びにこれらの光合成生物が作る有用物質の生産において有用に利用することができる。 As described above, according to the present invention, a solution obtained by dissolving incinerated ash with an acid contains nutrients necessary for the growth of photosynthetic organisms such as algae, and therefore can be used as a medium. . Further, since the culture medium of the present invention can cultivate photosynthetic organisms such as algae by shaking culture or aeration culture under light irradiation, culture of various photosynthetic organisms including chlorella and spirulina and production of organisms, In addition, it can be used effectively in the production of useful substances produced by these photosynthetic organisms.
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