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JP7474427B2 - Marine fertilizer, and manufacturing and installation methods for the same - Google Patents
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JP7474427B2 - Marine fertilizer, and manufacturing and installation methods for the same - Google Patents

Marine fertilizer, and manufacturing and installation methods for the same Download PDF

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JP7474427B2
JP7474427B2 JP2020005389A JP2020005389A JP7474427B2 JP 7474427 B2 JP7474427 B2 JP 7474427B2 JP 2020005389 A JP2020005389 A JP 2020005389A JP 2020005389 A JP2020005389 A JP 2020005389A JP 7474427 B2 JP7474427 B2 JP 7474427B2
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JP2021113137A (en
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善博 河津
浩一 福岡
民次 山本
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    • 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
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • 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
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/22Improving land use; Improving water use or availability; Controlling erosion

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Description

特許法第30条第2項適用 令和1年7月4日に、国立大学法人広島大学で開催された修士論文中間発表会での発表にて、海域施肥材、同海域施肥材の製造方法及び設置方法に関する研究について公開した。 令和1年9月5日~令和1年9月6日に、広島市西区民文化センターで開催された第27回(令和元年度)瀬戸内海研究フォーラムin広島での発表にて、海域施肥材、同海域施肥材の製造方法及び設置方法に関する研究について公開した。Application of Article 30, Paragraph 2 of the Patent Act Research on marine fertilization materials, and manufacturing and installation methods thereof was disclosed at a master's thesis interim presentation held at Hiroshima University, a national university corporation, on July 4, 2019. Research on marine fertilization materials, and manufacturing and installation methods thereof was disclosed at the 27th (2019) Seto Inland Sea Research Forum in Hiroshima, held at the Nishi Ward Community Center in Hiroshima City from September 5 to 6, 2019.

本発明は、海域施肥材、同海域施肥材の製造方法及び設置方法に関する。 The present invention relates to marine fertilizers, and manufacturing and installation methods for the marine fertilizers.

従来、アサリなどの植食性の二枚貝は、一般家庭の食卓や飲食店で提供される料理に至るまで、日本人の食生活において広く親しまれている。 Traditionally, herbivorous bivalve mollusks such as clams have been widely enjoyed in the Japanese diet, from being found on the dinner tables of ordinary households to being served in restaurants.

ところが、干潟等で得られるアサリの漁獲量は、近年減少傾向にある。これは、海水中の栄養塩の不足、例えば窒素やリン、鉄分などの不足による貧栄養化が原因であると考えられている。 However, the catch of clams caught in tidal flats and other areas has been declining in recent years. This is thought to be due to oligotrophy caused by a lack of nutrients in seawater, such as nitrogen, phosphorus, and iron.

そこで、二枚貝生育海域の貧栄養化の改善を図ることにより、二枚貝の漁獲量を回復させる試みがこれまでに幾つか提案されている。 Therefore, several attempts have been proposed to improve the oligotrophic conditions in the areas where bivalve mollusks grow, thereby restoring the bivalve mollusks' catches.

中でも、本願発明者の一人が過去に提案した植食性二枚貝の生育促進施肥材によれば、アサリを肥育させることができ、対照区画との比較から施肥材の施用により漁獲量の回復が見込まれる旨が記載されている(例えば、特許文献1参照)。 In particular, it has been described that a fertilizer for promoting the growth of herbivorous bivalve mollusks, previously proposed by one of the inventors of the present application, can fatten clams, and that application of the fertilizer is expected to restore catches in comparison with control plots (see, for example, Patent Document 1).

特開2017-158435号公報JP 2017-158435 A

しかしながら、上記従来の生育促進施肥材は、その構成材料が専ら無機肥料であったため持続性に欠けるものであった。その一方で、有機肥料は持続性に優れ、長期的な施肥効果を期待することが可能である。中でも、鶏糞を主原料としつつ十分に腐熟させることで所謂普通肥料として認められるに至った有機肥料は、特殊肥料の如き熟成度合いのやや低い有機肥料に比して周辺海域への環境的な負荷も更に少なく、有用な施肥材料の一つであると言える。 However, the above-mentioned conventional growth-promoting fertilizer materials were not sustainable because their constituent materials were mainly inorganic fertilizers. On the other hand, organic fertilizers are highly sustainable and can be expected to have a long-term fertilizing effect. In particular, organic fertilizers that use chicken manure as the main ingredient and have been fully decomposed to be recognized as so-called normal fertilizers place even less of a burden on the environment in the surrounding sea areas than organic fertilizers that are not fully matured, such as special fertilizers, and can be said to be one of the most useful fertilizing materials.

本発明は、斯かる事情に鑑みてなされたものであって、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現でき、更には二枚貝の成長と生残を効果的に上げることができる海域施肥材やその製造方法、及び設置方法を提供する。施肥材である The present invention was made in consideration of such circumstances, and provides a marine fertilizer, which is a highly sustainable organic fertilizer whose main component is derived from chicken manure, and which can dissolve nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks, and which can effectively increase the growth and survival of bivalve mollusks, as well as a manufacturing method and installation method for the same. The fertilizer is

上記従来の課題を解決するために、本発明に係る海域施肥材では、(1)12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水とを含む混合材料(ただし、同混合材料の全体を固化できる量のセメントが含まれたものを除く。)の圧縮成形体よりなり、海水にN/P=10~30、Fe/P=0.001~0.1の割合で溶出可能に構成した。 In order to solve the above-mentioned conventional problems, the marine fertilizer material of the present invention is (1) a compressed molded body of a mixed material containing 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water such that the moisture content of the marine fertilizer material described below is 45 to 60% by weight (excluding those that contain an amount of cement that is sufficient to solidify the entire mixed material) , and is configured to be soluble in seawater at a ratio of N/P = 10 to 30 and Fe/P = 0.001 to 0.1 .

また、本発明に係る海域施肥材の製造方法では、()12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水との混合材料(ただし、同混合材料の全体を固化できる量のセメントが含まれたものを除く。)を圧縮成形し海水にN/P=10~30、Fe/P=0.001~0.1の割合で溶出可能とすることとした。 In addition, in the manufacturing method of the marine fertilizer material according to the present invention, ( 2 ) a mixture of 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water such that the moisture content of the marine fertilizer material described below is 45 to 60% by weight (excluding those containing an amount of cement that can solidify the entire mixture) is compressed and molded to be soluble in seawater at a ratio of N/P = 10 to 30 and Fe/P = 0.001 to 0.1 .

また、本発明に係る海域施肥材の製造方法では、以下の点にも特徴を有する。
前記混合材料は、前記溶出のバランスが保たれる範囲内で腐葉土及び/または培養土を補助原料として含むこと
)前記発酵鶏糞は、鶏糞と同鶏糞よりも水分含量が低い水分調整材との混合物に対し鶏糞発酵微生物発酵液を添加して水分含量を60±5%に調整した被発酵混合物を調製する工程と、得られた被発酵混合物を堆積させて発酵を助長する工程と、被発酵混合物の温度が70℃以上となった際に、80℃に達する前に切り返しを行い、再び被発酵混合物を堆積させる切り返し工程と、水分含量が35%以下となり、且つ、温度が45℃以上に昇温しなくなるまで前記切り返し工程を繰り返す繰返工程と、繰返工程を経た被発酵混合物を、必要に応じ更なる追加発酵工程に供した上で発酵鶏糞とする発酵鶏糞生成工程と、を経て製造したものであることにも特徴を有する。
(5)前記鶏糞発酵微生物発酵液は、0.6重量部の乾燥ステビア茎粉末と、0.6重量部の米ぬか粉末と、0.6重量部の乾燥おから粉末と、耐塩性酵母を少なくとも含有する11~13重量部の汽水と、を混合した混合液を所定時間静置する静置工程と、前記静置工程を経た混合液を所定の容器に収容し、収容された混合液に同混合液の収容形状の外表面上のいずれの位置からも10cm以上であり、且つ、外表面上の少なくともいずれかの位置から17cm以下となる弱殺菌領域を形成する容器収容工程と、前記容器収容工程を経て混合液を収容した所定の容器を加熱空間内に配置し、同加熱空間を常温常圧の状態から約2.5気圧で150~160℃の状態にまで45~60分掛けて昇温し、約2.5気圧で150~160℃の状態を1~3分間維持し、その後加熱空間を約2気圧で115~125℃の状態にまで3~5分間掛けて降温設定し、約2気圧で115~125℃の状態を20~40分間維持し、更に加熱空間を常温常圧の状態にまで24~30時間掛けて降温させて、前記混合液中に加熱選抜された微生物を残存させる微生物選抜工程と、少なくとも微生物が液相に移行可能な手段により前記微生物選抜工程を経た混合液を固液分離して微生物含有液を得る固液分離工程と、得られた微生物含有液に糖源を添加して常温常圧で所定時間発酵し、微生物含有液のpHを4.5以下で、且つ、酸化還元電位を-100mV以下とする第1の発酵工程と、第1の発酵工程を経た微生物含有液にステビア茎の熟成液を添加してpHが3.1以下となるまで発酵させて不良発酵防止剤とする第2の発酵工程と、を経て得られた発酵液であること。
The method for producing a sea area fertilizer material according to the present invention is also characterized in the following points.
( 3 ) The mixed material contains leaf mold and/or culture soil as auxiliary raw materials within a range in which the balance of leaching is maintained .
( 4 ) The fermented chicken manure is also characterized in that it is produced through the steps of: preparing a fermented mixture by adding a chicken manure fermentation microorganism fermentation liquid to a mixture of chicken manure and a moisture regulator having a lower moisture content than the chicken manure to adjust the moisture content to 60±5%; piling the obtained fermented mixture to promote fermentation; a turning step in which, when the temperature of the fermented mixture reaches 70°C or higher, the mixture is turned over before it reaches 80°C and the fermented mixture is again turned over; a repeating step in which the turning step is repeated until the moisture content reaches 35% or less and the temperature does not rise to 45°C or higher; and a fermented chicken manure production step in which the fermented mixture that has been through the repeating step is subjected to a further additional fermentation step as necessary to produce fermented chicken manure.
(5) The chicken manure fermentation microorganism fermentation liquid is prepared by a process comprising a step of allowing a mixture of 0.6 parts by weight of dried stevia stem powder, 0.6 parts by weight of rice bran powder, 0.6 parts by weight of dried soybean pulp powder, and 11 to 13 parts by weight of brackish water containing at least a salt-tolerant yeast to stand for a predetermined period of time; a step of placing the mixture after the step in a predetermined container and forming a weakly sterilized region in the placed mixture that is 10 cm or more from any position on the outer surface of the placed shape of the mixture and 17 cm or less from at least any position on the outer surface; and a step of placing the container containing the mixture after the step in a heating space, raising the temperature of the heating space from room temperature and normal pressure to 150 to 160°C at about 2.5 atmospheres over 45 to 60 minutes, maintaining the state of 150 to 160°C at about 2.5 atmospheres for 1 to 3 minutes, and then placing the container in the heating space. a microorganism selection step in which the temperature of the mixture is lowered to 115-125°C at about 2 atmospheres over a period of 3-5 minutes, the state of 115-125°C at about 2 atmospheres is maintained for 20-40 minutes, and the temperature of the heating space is further lowered to room temperature and normal pressure over a period of 24-30 hours to leave the microorganisms selected by heating in the mixture; a solid-liquid separation step in which the mixture that has been through the microorganism selection step is solid-liquid separated by a means that allows at least the microorganisms to transfer to a liquid phase to obtain a microorganism-containing liquid; a first fermentation step in which a sugar source is added to the obtained microorganism-containing liquid and fermented at room temperature and normal pressure for a predetermined period of time to adjust the pH of the microorganism-containing liquid to 4.5 or less and the oxidation-reduction potential to -100 mV or less; and a second fermentation step in which a stevia stem aged liquid is added to the microorganism-containing liquid that has been through the first fermentation step, and fermented until the pH is 3.1 or less to obtain a defective fermentation inhibitor.

また、本発明に係る海域施肥材の設置方法では、()前記(1)に記載の海域施肥材又は前記()~()のいずれか1つに記載の海域施肥材の製造方法にて製造された海域施肥材の設置方法であって、海域施肥材の高さと同程度の穴を干潟に形成して設置する工程と、形成した穴に海域施肥材を配置したのち、同海域施肥材の上部をわずかの砂で被覆する工程と、を有することとした。 In addition, the method for installing a marine fertilization material according to the present invention is ( 6 ) a method for installing a marine fertilization material manufactured by the marine fertilization material described in (1) above or the manufacturing method for a marine fertilization material described in any one of ( 2 ) to ( 5 ) above, comprising the steps of forming a hole in the tidal flat to the same height as the marine fertilization material and installing the material, and placing the marine fertilization material in the formed hole, and then covering the top of the marine fertilization material with a small amount of sand.

本発明に係る海域施肥材によれば、12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水とを含む混合材料(ただし、同混合材料の全体を固化できる量のセメントが含まれたものを除く。)の圧縮成形体よりなり、海水にN/P=10~30、Fe/P=0.001~0.1の割合で溶出可能に構成したため、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現でき、更には二枚貝の成長と生残を効果的に上げることが可能な海域施肥材とすることができる。 The marine fertilizer of the present invention is made of a compressed molded body of a mixed material containing 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water such that the moisture content of the marine fertilizer described below is 45 to 60% by weight (excluding those containing an amount of cement that can solidify the entire mixed material). It is configured to be soluble in seawater at a ratio of N/P = 10 to 30 and Fe/P = 0.001 to 0.1, so it is an organic fertilizer with excellent sustainability, and while its main constituent material is derived from chicken manure, it can realize the elution of nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks, and can also be a marine fertilizer that can effectively increase the growth and survival of bivalve mollusks.

また、前記酸化マグネシウムは、前記発酵鶏糞由来のリンの溶出の調整を目的として添加すれば、リンの豊富な鶏糞を原料の一つとしながらも、過剰なリンの溶出を抑制し、藻類の生育に適した栄養成分の溶出比を実現することができる。 In addition, if the magnesium oxide is added for the purpose of adjusting the elution of phosphorus derived from the fermented chicken manure, it is possible to suppress the elution of excess phosphorus while using phosphorus-rich chicken manure as one of the raw materials, and to achieve an elution ratio of nutrients suitable for algae growth.

また、高さ10~30cm、幅15~30cmの柱状とすれば、海域施肥材に更なる徐放性を付与することができ、持続性により優れた海域施肥材とすることができる。 In addition, if the material is made into a column shape measuring 10-30 cm in height and 15-30 cm in width, the marine fertilizer can be given even more sustained release properties, making it a more sustainable marine fertilizer.

また、前記発酵鶏糞は、鶏糞と同鶏糞よりも水分含量が低い水分調整材との混合物に対し鶏糞発酵微生物発酵液を添加して水分含量を60±5%に調整した被発酵混合物を調製する工程と、得られた被発酵混合物を堆積させて発酵を助長する工程と、被発酵混合物の温度が70℃以上となった際に、80℃に達する前に切り返しを行い、再び被発酵混合物を堆積させる切り返し工程と、水分含量が35%以下となり、且つ、温度が45℃以上に昇温しなくなるまで前記切り返し工程を繰り返す繰返工程と、繰返工程を経た被発酵混合物を、必要に応じ更なる追加発酵工程に供した上で発酵鶏糞とする発酵鶏糞生成工程と、を経て製造したものであることとすれば、十分に腐熟した発酵鶏糞とすることができ、不完全な発酵に由来する海洋への環境負荷を可及的に抑制することができる。 In addition, if the fermented chicken manure is produced through the steps of: preparing a fermented mixture by adding a chicken manure fermentation microorganism fermentation liquid to a mixture of chicken manure and a moisture regulator having a lower moisture content than the chicken manure to adjust the moisture content to 60±5%; piling the obtained fermented mixture to promote fermentation; turning the fermented mixture when the temperature of the fermented mixture reaches 70°C or higher before it reaches 80°C and piling the fermented mixture again; repeating the turning process until the moisture content is 35% or less and the temperature does not rise to 45°C or higher; and a fermented chicken manure production process in which the fermented mixture that has been through the repeating process is subjected to an additional fermentation process as necessary to produce fermented chicken manure, then the fermented chicken manure that has been produced through the steps can be sufficiently decomposed, and the environmental load on the ocean caused by incomplete fermentation can be suppressed as much as possible.

また、前記鶏糞発酵微生物発酵液は、0.6重量部の乾燥ステビア茎粉末と、0.6重量部の米ぬか粉末と、0.6重量部の乾燥おから粉末と、耐塩性酵母を少なくとも含有する11~13重量部の汽水と、を混合した混合液を所定時間静置する静置工程と、前記静置工程を経た混合液を所定の容器に収容し、収容された混合液に同混合液の収容形状の外表面上のいずれの位置からも10cm以上であり、且つ、外表面上の少なくともいずれかの位置から17cm以下となる弱殺菌領域を形成する容器収容工程と、前記容器収容工程を経て混合液を収容した所定の容器を加熱空間内に配置し、同加熱空間を常温常圧の状態から約2.5気圧で150~160℃の状態にまで45~60分掛けて昇温し、約2.5気圧で150~160℃の状態を1~3分間維持し、その後加熱空間を約2気圧で115~125℃の状態にまで3~5分間掛けて降温設定し、約2気圧で115~125℃の状態を20~40分間維持し、更に加熱空間を常温常圧の状態にまで24~30時間掛けて降温させて、前記混合液中に加熱選抜された微生物を残存させる微生物選抜工程と、少なくとも微生物が液相に移行可能な手段により前記微生物選抜工程を経た混合液を固液分離して微生物含有液を得る固液分離工程と、得られた微生物含有液に糖源を添加して常温常圧で所定時間発酵し、微生物含有液のpHを4.5以下で、且つ、酸化還元電位を-100mV以下とする第1の発酵工程と、第1の発酵工程を経た微生物含有液にステビア茎の熟成液を添加してpHが3.1以下となるまで発酵させて不良発酵防止剤とする第2の発酵工程と、を経て得られた発酵液であることとすれば、鶏糞の発酵をより堅実に行うことができる。 The chicken manure fermentation microorganism fermentation liquid is prepared by mixing 0.6 parts by weight of dried stevia stem powder, 0.6 parts by weight of rice bran powder, 0.6 parts by weight of dried soybean pulp powder, and 11 to 13 parts by weight of brackish water containing at least a salt-tolerant yeast, in a step of leaving the mixture for a predetermined period of time, a step of placing the mixture that has undergone the step of leaving the mixture in a predetermined container, and forming a weakly sterilized area in the placed mixture that is 10 cm or more from any position on the outer surface of the shape of the mixture and 17 cm or less from at least any position on the outer surface, and a step of placing the predetermined container that has contained the mixture that has undergone the step of placing the mixture in a heating space, raising the temperature of the heating space from room temperature and pressure to a state of 150 to 160°C at about 2.5 atmospheres over a period of 45 to 60 minutes, maintaining the state of 150 to 160°C at about 2.5 atmospheres for 1 to 3 minutes, and then heating the heating space to a state of 115 to 120°C at about 2 atmospheres. 5°C over 3-5 minutes, maintaining a temperature of 115-125°C at approximately 2 atm for 20-40 minutes, and further lowering the temperature of the heating space to room temperature and normal pressure over 24-30 hours to leave the heat-selected microorganisms in the mixed liquid; a solid-liquid separation process in which the mixed liquid that has been through the microorganism selection process is solid-liquid separated by a means that allows at least the microorganisms to transition to a liquid phase to obtain a microorganism-containing liquid; a first fermentation process in which a sugar source is added to the obtained microorganism-containing liquid and fermented at room temperature and normal pressure for a predetermined time to set the pH of the microorganism-containing liquid to 4.5 or less and the oxidation-reduction potential to -100 mV or less; and a second fermentation process in which a stevia stem aged liquid is added to the microorganism-containing liquid that has been through the first fermentation process and fermented until the pH is 3.1 or less to obtain a defective fermentation inhibitor. This allows for more reliable fermentation of chicken manure.

また、本発明に係る海域施肥材の製造方法によれば、12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水との混合材料(ただし、同混合材料の全体を固化できる量のセメントが含まれたものを除く。)を圧縮成形し海水にN/P=10~30、Fe/P=0.001~0.1の割合で溶出可能としたため、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現でき、更には二枚貝の成長と生残を効果的に上げることができる海域施肥材を製造することができる。 In addition, according to the manufacturing method of the marine fertilizer material of the present invention, a mixture of 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water such that the moisture content of the marine fertilizer material described below is 45 to 60% by weight (excluding those containing an amount of cement that can solidify the entire mixture). It is then compressed and molded into seawater so that it can be dissolved in a ratio of N/P = 10 to 30 and Fe/P = 0.001 to 0.1. This makes it possible to produce a marine fertilizer that is a highly sustainable organic fertilizer that is mainly composed of chicken manure and can dissolve nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks, and can effectively increase the growth and survival of bivalve mollusks.

また、前記酸化マグネシウムは、前記発酵鶏糞由来のリンの溶出を調整するために添加していることとすれば、リンの豊富な鶏糞を原料の一つとしながらも、過剰なリンの溶出を抑制し、藻類の生育に適した栄養成分の溶出比を実現することができる。 In addition, if the magnesium oxide is added to adjust the elution of phosphorus derived from the fermented chicken manure, it is possible to suppress the elution of excess phosphorus while using chicken manure, which is rich in phosphorus, as one of the raw materials, and to achieve an elution ratio of nutrients suitable for algae growth.

また、本発明に係る海域施肥材の設置方法によれば、上述の海域施肥材又は海域施肥材の製造方法にて製造された海域施肥材の設置方法であって、海域施肥材の高さと同程度の穴を干潟に形成して設置する工程と、形成した穴に海域施肥材を配置したのち、同海域施肥材の上部をわずかの砂で被覆する工程と、を有することとしたため、海域施肥材の設置が容易でありながら、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現可能な海域施肥材としての効果を良好に発揮させることができる。 In addition, according to the method for installing marine fertilization material of the present invention, the method for installing the above-mentioned marine fertilization material or marine fertilization material manufactured by the manufacturing method for marine fertilization material includes the steps of forming a hole in the tidal flat with a height equivalent to that of the marine fertilization material and installing the material, and placing the marine fertilization material in the hole and then covering the top of the marine fertilization material with a small amount of sand. This makes it easy to install the marine fertilization material, and it is an organic fertilizer with excellent long-lasting properties, and its main component is derived from chicken manure, and it is capable of dissolving nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks, and it can effectively exert its effect as a marine fertilization material.

粒状鉄の使用量を変化させた場合の溶出比(Fe/P)の違いを示した説明図である。FIG. 2 is an explanatory diagram showing the difference in elution ratio (Fe/P) when the amount of granular iron used is changed. 酸化マグネシウムの使用量を変化させた場合の各成分の溶出状況の違いを示した説明図である。FIG. 1 is an explanatory diagram showing the difference in the elution state of each component when the amount of magnesium oxide used is changed. フィールド試験の結果を示す説明図である。FIG. 13 is an explanatory diagram showing the results of a field test.

本発明は、海域施肥材に関するものであり、特に、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる付着微細藻または底生微細藻の生育に適した栄養成分の溶出を実現でき、更には二枚貝の成長と生残を効果的に上げることができる海域施肥材を提供するものである。 The present invention relates to a marine fertilizer, and in particular to a marine fertilizer that is a highly sustainable organic fertilizer whose main component is derived from chicken manure, and that can dissolve nutrients suitable for the growth of attached or benthic microalgae that serve as food for herbivorous bivalve mollusks, and can effectively increase the growth and survival of the bivalve mollusks.

藻類、特に植物プランクトンや付着性の微細藻類(以下、単に藻類と称する。)は、海域の主要な基礎生産を担っており、これらが二枚貝の餌となっている。従って、貧栄養海域にて二枚貝の餌となる藻類の増殖が促されると、結果的に二枚貝の増殖が促される。 Algae, especially phytoplankton and periphyton microalgae (hereafter simply referred to as algae), are the main primary producers in the ocean, and they are food for bivalve mollusks. Therefore, if the proliferation of algae, which serves as food for bivalve mollusks, is promoted in oligotrophic ocean areas, the proliferation of bivalve mollusks is promoted as a result.

藻類が増殖するためには、所定の栄養素が必要である。この栄養素は、窒素(N)、リン酸(P)、カリウム(K)を要求する陸上作物とは異なっており、N:Si:P:Fe=16:15:1:0.005であることが知られている。 Algae need certain nutrients to grow. These nutrients differ from those required by land crops, which require nitrogen (N), phosphorus (P), and potassium (K), and are known to have a ratio of N:Si:P:Fe=16:15:1:0.005.

しかしながら、化成肥料などではなく有機肥料を主要な構成材料としつつ、このような成分溶出比を実現した海域施肥材は提供されていない。 However, no marine fertilizer has been provided that uses organic fertilizers, rather than chemical fertilizers, as its main component and achieves such a component elution ratio.

そこで、本実施形態に係る海域施肥材では、その特徴的な構成として、12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水とを含む圧縮成形体よりなることとしている。 The marine fertilizer material according to this embodiment is characterized by its composition being a compressed molded body containing 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water such that the moisture content of the marine fertilizer material described below is 45 to 60% by weight.

ここで発酵鶏糞は、鶏舎より得られる排泄直後の鶏糞(所謂、生鶏糞)ではなく、発酵により腐熟させた鶏糞である。発酵の過程は特に限定されるものではないが、後述の発酵過程を経ることで、良質な腐熟を行わせることができる。 The fermented chicken manure referred to here is not chicken manure obtained from the chicken coop immediately after excretion (so-called raw chicken manure), but chicken manure that has been decomposed by fermentation. The fermentation process is not particularly limited, but by going through the fermentation process described below, high-quality decomposition can be achieved.

粒状鉄は、鉄分の溶出をもたらす原料である。粒状とは、一乃至は幾つかの塊状の鉄ではなく、より細かく多数(複数)であることを意味するものであり、砂鉄の如く粉状のものも含む。粒状鉄は、例えば直径が概ね0.05mm~10mm程度とすることができ、具体的には鉄鋼スラグ粒や砂鉄、鉄粉などを利用することができる。 Granular iron is a raw material that causes iron to dissolve. Granular does not mean one or several lumps of iron, but rather means that it is finer and numerous (multiple), and includes powder-like iron such as iron sand. Granular iron can have a diameter of, for example, approximately 0.05 mm to 10 mm, and specific examples that can be used include steel slag granules, iron sand, and iron powder.

粒状鉄の使用量は、発酵鶏糞の使用量を12重量部とした場合、2重量部以上、例えば2~6重量部に相当する量を使用する。ここで粒状鉄の添加量が2重量部を下回ると鉄分の不足という問題があるため好ましくない。粒状鉄の使用量を2重量部以上とすることで、最適な鉄分の供給を実現することができる。 The amount of granular iron used should be at least 2 parts by weight, for example 2 to 6 parts by weight, assuming that the amount of fermented chicken manure used is 12 parts by weight. Adding less than 2 parts by weight of granular iron is not preferred as this can lead to problems such as iron deficiency. By using 2 parts by weight or more of granular iron, an optimal supply of iron can be achieved.

酸化マグネシウムは、本実施形態に係る海域施肥材において固化剤として機能すると共に、同海域施肥材からのリンの溶出を調整する役割を有するものであり、市販の酸化マグネシウムを利用することができる。酸化マグネシウムは粉末の状態で添加しても良く、また必要に応じ水に溶解させて添加しても良い。 Magnesium oxide functions as a solidifying agent in the marine fertilizer of this embodiment and also has the role of adjusting the elution of phosphorus from the marine fertilizer, and commercially available magnesium oxide can be used. Magnesium oxide may be added in powder form, or may be dissolved in water and added as necessary.

酸化マグネシウムの使用量は、発酵鶏糞の使用量を12重量部とした場合、1~4重量部に相当する量を使用する。ここで酸化マグネシウムの添加量が1重量部を下回ると硬度不足という問題があるため好ましくない。また4重量部を上回ると、リン酸の溶出が過度に抑制されてしまうという問題があるため好ましくない。酸化マグネシウムの使用量を1~4重量部とすることで、最適なリン酸の供給を実現することができる。 The amount of magnesium oxide used is equivalent to 1 to 4 parts by weight, assuming that the amount of fermented chicken manure used is 12 parts by weight. Adding less than 1 part by weight of magnesium oxide is not preferred because it will cause a problem of insufficient hardness. Adding more than 4 parts by weight is also not preferred because it will cause a problem of excessive suppression of phosphoric acid elution. By using 1 to 4 parts by weight of magnesium oxide, an optimal supply of phosphoric acid can be achieved.

また、本実施形態に係る海域施肥材には、その他の補助原料を添加してもよい。この補助原料としては、例えば腐葉土や培養土等が挙げられる。これら補助原料は、本願発明の目的の達成を阻害しない窒素(N)やリン酸(P)、カリウム(K)、鉄などの溶出バランスが保たれる範囲において、その量や成分などを適宜選択することができる。 In addition, other auxiliary materials may be added to the marine fertilizer material according to this embodiment. Examples of such auxiliary materials include leaf mold and culture soil. The amount and components of these auxiliary materials can be appropriately selected within a range that maintains a balance of dissolution of nitrogen (N), phosphorus (P), potassium (K), iron, etc. that does not impede the achievement of the object of the present invention.

そして、これら12重量部の発酵鶏糞に対し、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムとを混合し、必要に応じて補助原料を添加した混合物の水分含量を45~60重量%に調整する。換言すれば、混合物に対し、同混合物の水分含量が45~60重量%となる量の水分を添加する。 Then, 2 to 6 parts by weight of granular iron and 1 to 4 parts by weight of magnesium oxide are mixed with 12 parts by weight of the fermented chicken manure, and auxiliary ingredients are added as necessary to adjust the moisture content of the mixture to 45 to 60% by weight. In other words, water is added to the mixture in an amount that will result in a moisture content of 45 to 60% by weight.

この水分調整混合物を所定の圧縮成形機に供して圧縮成形することで、本実施形態に係る海域施肥材を得ることができる。 This moisture-adjusted mixture can be subjected to compression molding in a specified compression molding machine to obtain the marine fertilizer material according to this embodiment.

すなわち、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出、例えば、N/P=10~30でFe/P=0.001~0.1の溶出を実現でき、更には二枚貝の成長と生残を効果的に上げることができる海域施肥材を提供することができる。 In other words, it is possible to provide a marine fertilizer that is a highly sustainable organic fertilizer whose main component is derived from chicken manure, and that can dissolve nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks, for example, N/P = 10-30 and Fe/P = 0.001-0.1, and can also effectively increase the growth and survival of bivalve mollusks.

なお、この海域施肥材は、圧縮成形されていれば特にその形状は限定されるものではないが、例えばペレット状乃至は柱状の外観とすることができる。また、その大きさも限定されるものではなく、例えば、高さ10~30cm、幅15~30cmの柱状とすることで、持続性に優れた海域施肥材とすることが可能である。またこの場合、面積/体積比は、0.1~0.9程度、より限定的には0.2~0.5程度を目安とすることができる。なお、圧縮成形圧力は0.4平方メートルあたり300kgf以上が好ましく、例えば0.4平方メートルあたり0.5~1.0トンとすることができる。 The marine fertilizer material is not particularly limited in shape as long as it is compressed and molded, but it can have a pellet-like or columnar appearance, for example. The size is also not limited, and by making it into a columnar shape with a height of 10 to 30 cm and a width of 15 to 30 cm, it can become a marine fertilizer material with excellent durability. In this case, the area/volume ratio can be approximately 0.1 to 0.9, or more specifically, approximately 0.2 to 0.5. The compression molding pressure is preferably 300 kgf or more per 0.4 square meters, and can be, for example, 0.5 to 1.0 ton per 0.4 square meters.

また、前記発酵鶏糞は、被発酵混合物を調製する工程と、発酵を助長する工程と、切り返し工程と、繰返工程と、発酵鶏糞生成工程と、を経て製造したものとするのが好ましい。 The fermented chicken manure is preferably produced through a process of preparing a fermented mixture, a process of promoting fermentation, a process of turning over, a process of repeating, and a process of producing fermented chicken manure.

被発酵混合物を調製する工程は、鶏糞と同鶏糞よりも水分含量が低い水分調整材との混合物に対し鶏糞発酵微生物発酵液を添加して水分含量を60±5%の範囲内に調整する工程である。水分含量調整材としては、例えば、上述の各工程を経て得られた発酵鶏糞、その他乾燥したオガクズ等を利用することができる。 The process for preparing the fermented mixture involves adding a fermentation liquid of a chicken manure fermenting microorganism to a mixture of chicken manure and a moisture regulator with a lower moisture content than the chicken manure to adjust the moisture content to within the range of 60±5%. As the moisture content regulator, for example, the fermented chicken manure obtained through each of the above processes or other dried sawdust can be used.

発酵を助長する工程は、得られた被発酵混合物を堆積させることで行われる。堆積は、例えばコンクリート等で三方が囲われた屋根付きの発酵ヤード等で行うことができ、発酵量にもよるが、高さは概ね1.8~2.0m程度とすることができる。 The process of promoting fermentation is carried out by piling up the resulting fermented mixture. Piling can be carried out, for example, in a roofed fermentation yard surrounded on three sides by concrete or the like, and although it depends on the amount of fermentation, the height can be approximately 1.8 to 2.0 m.

切り返し工程は、被発酵混合物の温度が70℃以上となった際に、80℃に達する前に切り返しを行い、再び被発酵混合物を堆積させる工程である。切り返しを行うことで、発酵を行う乳酸菌や酵母の至適温度帯としつつ、堆積させた被発酵混合物中に酸素を供給できる。 The turning process is a process in which the fermented mixture is turned when its temperature reaches 70°C or higher, before it reaches 80°C, and the fermented mixture is piled up again. By turning the mixture, oxygen can be supplied to the piled up fermented mixture while maintaining the optimum temperature range for the lactic acid bacteria and yeast that perform the fermentation.

繰返工程は、上記切り返し工程を繰り返し行う工程であり、被発酵混合物の水分含量が35%以下となり、且つ、温度が45℃以上に昇温しなくなるまで行う。なお、季節や温度により異なるため一応の目安であるが、この繰返工程を含め、切り返し工程は概ね3~5回程度行われて、次の発酵鶏糞生成工程が行われる。 The repeating process is a process in which the above-mentioned turning process is repeated until the moisture content of the fermented mixture falls below 35% and the temperature does not rise above 45°C. Note that this is only a rough guideline as it varies depending on the season and temperature, but the turning process, including this repeating process, is generally carried out about 3 to 5 times before the next fermented chicken manure production process is carried out.

発酵鶏糞生成工程は、繰返工程を経た被発酵混合物を、必要に応じ更なる追加発酵工程に供した上で発酵鶏糞とする工程である。すなわち、この繰り返し工程を経て得られた被発酵混合物を本工程においてそのまま発酵鶏糞としても良いし、更なる追加発酵工程に供した後に発酵鶏糞とすることも可能である。 The fermented chicken manure production process is a process in which the fermented mixture obtained through the repeating process is subjected to a further additional fermentation process as necessary to produce fermented chicken manure. That is, the fermented mixture obtained through this repeating process may be directly used as fermented chicken manure in this process, or it may be used as fermented chicken manure after being subjected to a further additional fermentation process.

本工程で必要に応じて行う追加発酵工程としては、繰返工程を経た被発酵混合物を壁にもたれ掛けさせるように高く(例えば、2m以上)堆積させ、自重でその下部を圧縮させながら1ヶ月に1~2度切り返しつつ発酵を行わせる。 As an additional fermentation step that may be performed as necessary in this process, the fermented mixture that has gone through the repeated process is piled up high (for example, 2m or more) so that it is leaned against a wall, and fermentation is carried out while compressing the lower part under its own weight and turning it over once or twice a month.

この追加発酵工程は、例えば、水分含量が20%以下で、窒素分が2.8%以上、リン酸が3.8%以上、カリが3.0%以上となるまで切り返しつつ、発酵・熟成を行って、発酵鶏糞とするのが好ましい。 In this additional fermentation process, it is preferable to ferment and mature the manure while turning it over until the moisture content is 20% or less, the nitrogen content is 2.8% or more, the phosphoric acid content is 3.8% or more, and the potassium content is 3.0% or more, to produce fermented chicken manure.

また前述の鶏糞発酵微生物発酵液は、底質環境改善の対象領域に存在する余剰な有機物、例えばヘドロ状となった領域が存在する底質環境を改善できる微生物(以下、鶏糞発酵微生物とも称する。)によって発酵され鶏糞発酵微生物の代謝産物を含有する液であるが、本願では、被発酵混合物中において鶏糞の発酵や熟成を行う菌叢を形成させるためのスタータとして機能させるために使用する点で特徴的である。 The aforementioned chicken manure fermentation microorganism fermentation liquid is a liquid that is fermented by microorganisms (hereinafter also referred to as chicken manure fermentation microorganisms) that can improve the bottom sediment environment where excess organic matter exists in the target area for bottom sediment environment improvement, such as areas that have become sludge-like, and contains metabolic products of the chicken manure fermentation microorganisms. In the present application, however, it is characterized in that it is used to function as a starter for forming a bacterial flora that ferments and matures chicken manure in the fermentation mixture.

この鶏糞発酵微生物の種類は特に限定されるものではないが、例えば、後述する汽水領域より採取した汽水中に含まれる微生物群の中から、後述のスクリーニング手法に従い選抜された微生物、特に、好塩性(耐塩性)の酵母を多く含んだ細菌叢を用いる。 The type of chicken manure fermentation microorganism is not particularly limited, but for example, microorganisms selected from the microbial population contained in brackish water collected from the brackish water area described below using a screening method described below, in particular a bacterial flora containing a large amount of halophilic (salt-tolerant) yeast, are used.

すなわち、鶏糞発酵微生物発酵液は、上述の鶏糞発酵微生物の発酵による発酵代謝産物が含まれ、菌勢や菌量が高められた液であれば特に限定されるものではないが、例えば以下に説明する所定の静置工程と、容器収容工程と、微生物選抜工程と、固液分離工程と、第1の発酵工程と、第2の発酵工程とを経て製造された液を採用することができる。これら工程を経ることにより、汽水由来の好塩性(耐塩性)酵母を中心とし、その他原料等に由来する微生物群(例えば乳酸菌群など)との共生によって鶏糞の発酵や熟成に優れ、藻類の生育に適した栄養成分の生成に寄与する。 In other words, the chicken manure fermentation microorganism fermentation liquid is not particularly limited as long as it contains fermentation metabolic products produced by the fermentation of the chicken manure fermentation microorganisms described above and is a liquid in which the bacterial activity and amount are increased, but for example, a liquid produced through a predetermined settling step, container placement step, microbial selection step, solid-liquid separation step, first fermentation step, and second fermentation step described below can be used. By going through these steps, the chicken manure is excellent in fermentation and maturation due to the symbiosis of brackish water-derived halophilic (salt-tolerant) yeast and other microorganisms derived from the raw materials (e.g., lactic acid bacteria), and contributes to the production of nutritional components suitable for algae growth.

ここで静置工程は、不良発酵防止剤に含まれるエキス分の抽出原料となる資材(以下、総称してエキス抽出資材ともいう。)と、好塩性(耐塩性)の酵母を少なくとも含有する汽水とを混合し、静置しながら汽水中にエキス分を溶出させる工程であり、0.6重量部の乾燥ステビア茎粉末と、0.6重量部の米ぬか粉末と、0.6重量部の乾燥おから粉末と、好塩性(耐塩性)の酵母を少なくとも含有する11~13重量部の汽水と、を混合した混合液を所定時間静置する工程である。本静置工程では、これらエキス抽出資材と汽水とを所定量ずつ混合し、例えば常温にて所定時間静置する。静置に要する時間は、例えば15~20日間とすることができる。 The settling step is a step of mixing materials (hereinafter collectively referred to as extract extraction materials) that are the raw materials for extracting the extract contained in the defective fermentation inhibitor with brackish water containing at least halophilic (salt-tolerant) yeast, and dissolving the extract into the brackish water while standing still. This is a step of standing still for a predetermined period of time for a mixture of 0.6 parts by weight of dried stevia stem powder, 0.6 parts by weight of rice bran powder, 0.6 parts by weight of dried soybean pulp powder, and 11 to 13 parts by weight of brackish water containing at least halophilic (salt-tolerant) yeast. In this settling step, predetermined amounts of the extract extraction materials and brackish water are mixed and left to stand for a predetermined period of time, for example, at room temperature. The time required for standing can be, for example, 15 to 20 days.

また、容器収容工程は、前記静置工程を経た混合液を所定の容器に収容し、収容された混合液に同混合液の収容形状の外表面上のいずれの位置からも10cm以上であり、且つ、外表面上の少なくともいずれかの位置から17cm以下となる弱殺菌領域を形成して後述の微生物選抜工程において加熱した際に完全滅菌が行われないようにする工程である。 The container placement process is a process in which the mixed liquid that has been through the settling process is placed in a specified container, and a weak sterilization area is formed in the placed mixed liquid that is 10 cm or more from any position on the outer surface of the container shape of the mixed liquid, and 17 cm or less from at least any position on the outer surface, so that complete sterilization does not occur when the mixed liquid is heated in the microorganism selection process described below.

また、微生物選抜工程は、前記容器収容工程を経て混合液を収容した所定の容器を加熱空間内に配置し、同加熱空間を常温常圧の状態から約2.5気圧で150~160℃の状態にまで45~60分掛けて昇温し、約2.5気圧で150~160℃の状態を1~3分間維持して第1の加熱工程を行い、その後加熱空間を約2気圧で115~125℃の状態にまで3~5分間掛けて降温設定し、約2気圧で115~125℃の状態を20~40分間維持して第2の加熱工程を行い、更に加熱空間を常温常圧の状態にまで24~30時間掛けて降温させて降温工程を行い、前記混合液中に加熱選抜された微生物を残存させる工程である。 The microorganism selection process is a process in which a specified container containing the mixed liquid after the container placement process is placed in a heating space, the heating space is heated from room temperature and normal pressure to 150-160°C at about 2.5 atmospheres over 45-60 minutes, the state of 150-160°C at about 2.5 atmospheres is maintained for 1-3 minutes to perform the first heating process, the heating space is then cooled to 115-125°C at about 2 atmospheres over 3-5 minutes, the state of 115-125°C at about 2 atmospheres is maintained for 20-40 minutes to perform the second heating process, and the heating space is further cooled to room temperature and normal pressure over 24-30 hours to perform the cooling process, thereby leaving the microorganisms selected by heating in the mixed liquid.

また、固液分離工程は、少なくとも微生物が液相に移行可能な手段により前記微生物選抜工程を経た混合液を固液分離して微生物含有液を得る工程である。固液分離は、必ずしも完全に固形分を除去する必要はなく、選抜した微生物を液相に移行させながら大まかに固形分を除き流動性を向上させる程度のイメージである。このような固液分離は、例えば布製の袋等に混合液を収容し、洗濯機の脱水機能等を利用して行うことができる。また、一般の固液分離装置を利用して微生物を液相に残せる程度の遠心力を付与して固液分離を行うようにしても良いし、同じく布製の袋に混合液を収容して搾汁することで液相を得ても良い。 The solid-liquid separation process is a process for obtaining a microorganism-containing liquid by performing solid-liquid separation on the mixed liquid that has been through the microorganism selection process using a means that allows at least the microorganisms to migrate to the liquid phase. Solid-liquid separation does not necessarily require complete removal of solids, but is merely an idea of roughly removing solids and improving fluidity while transferring the selected microorganisms to the liquid phase. Such solid-liquid separation can be performed, for example, by placing the mixed liquid in a cloth bag or the like and using the spin-drying function of a washing machine. Alternatively, solid-liquid separation can be performed by applying a centrifugal force sufficient to leave the microorganisms in the liquid phase using a general solid-liquid separation device, or the mixed liquid can be placed in a cloth bag and squeezed to obtain the liquid phase.

また、第1の発酵工程は、得られた微生物含有液に糖源を添加して常温常圧で所定時間発酵させ、微生物含有液のpHを4.5以下で、且つ、酸化還元電位を-100mV以下とする工程である。 The first fermentation process is a process in which a sugar source is added to the obtained microorganism-containing liquid and fermented at room temperature and pressure for a predetermined time, so that the pH of the microorganism-containing liquid is 4.5 or less and the redox potential is -100 mV or less.

また、第2の発酵工程は、第1の発酵工程を経た微生物含有液にステビア茎の熟成液を添加してpHが3.1以下となるまで発酵させて不良発酵防止剤とする工程である。微生物含有液に対するステビア茎熟成液の添加量は、微生物含有液0.38重量部に対して0.38~0.4重量部程度とすることができる。 The second fermentation process is a process in which a stevia stem matured liquid is added to the microorganism-containing liquid that has been through the first fermentation process, and fermented until the pH is 3.1 or less to produce a defective fermentation inhibitor. The amount of stevia stem matured liquid added to the microorganism-containing liquid can be about 0.38 to 0.4 parts by weight per 0.38 parts by weight of the microorganism-containing liquid.

ここで、本第2の発酵工程にて使用するステビア茎の熟成液は、ステビア茎を水等に浸漬してエキス分を抽出しつつ、ステビア茎由来の微生物によって発酵を行うことにより得られた発酵液(以下、ステビア茎簡易熟成液ともいう。)を用いることもできる。 Here, the stevia stem matured liquid used in this second fermentation step can be a fermented liquid obtained by soaking stevia stems in water or the like to extract the extract while fermenting with microorganisms derived from stevia stems (hereinafter also referred to as a simple stevia stem matured liquid).

しかしながら、ステビア茎の熟成液は、ステビア茎分散液調製工程と、ステビア茎分散液容器収容工程と、ステビア茎由来微生物選抜工程と、ステビア茎抽出液調製工程と、抽出液濃縮工程と、熟成工程と、を経て調製するのがより望ましい。 However, it is more preferable to prepare the stevia stem matured liquid through a stevia stem dispersion preparation process, a stevia stem dispersion container placement process, a stevia stem-derived microorganism selection process, a stevia stem extract preparation process, an extract concentration process, and a maturation process.

ステビア茎分散液調製工程は、乾燥ステビア茎の粉末に水を加えてステビア茎の分散液を調製する工程であり、具体的には、1重量部の乾燥ステビア茎粉末に対して10重量部±2重量部程度の水を添加して調製する。 The stevia stem dispersion preparation process is a process in which water is added to dried stevia stem powder to prepare a stevia stem dispersion. Specifically, the process is carried out by adding approximately 10 parts by weight ± 2 parts by weight of water to 1 part by weight of dried stevia stem powder.

ステビア茎分散液容器収容工程は、前述の容器収容工程と略同様に後述のステビア茎由来微生物選抜工程において加熱した際に完全滅菌が行われないよう、弱殺菌領域を形成可能な容器に収容する工程である。 The stevia stem dispersion container placement process is a process in which the stevia stem dispersion is placed in a container capable of forming a weak sterilization region so that complete sterilization does not occur when heated in the stevia stem-derived microorganism selection process described below, in a manner similar to the container placement process described above.

このステビア茎分散液容器収容工程における弱殺菌領域は、所定の容器内に収容したステビア茎分散液の収容形状のうち、外表面上のいずれの位置からも10cm以上であり、且つ、外表面上の少なくともいずれかの位置から17cm以下となる内部領域である。より好ましくは、外表面上のいずれの位置からも17cmを越える非選抜領域が形成されず弱殺菌領域を形成可能な容器を用いる。 The weakly sterilized region in this stevia stem dispersion container placement process is an internal region that is 10 cm or more from any position on the outer surface and 17 cm or less from at least any position on the outer surface of the container in which the stevia stem dispersion is placed. More preferably, a container is used that is capable of forming a weakly sterilized region without forming a non-selected region that is more than 17 cm from any position on the outer surface.

ステビア茎由来微生物選抜工程もまた前述の微生物選抜工程と同様、ステビア茎分散液を加熱して、ステビア茎由来の微生物を選抜する工程であり、細かくは第1のステビア茎加熱工程と、第2のステビア茎加熱工程とで構成される。 The stevia stem-derived microorganism selection process, like the above-mentioned microorganism selection process, is a process in which a stevia stem dispersion is heated to select microorganisms derived from stevia stems, and more specifically, it is composed of a first stevia stem heating process and a second stevia stem heating process.

第1のステビア茎加熱工程は、ステビア茎分散液容器収容工程を経てステビア茎分散液を収容した所定の容器を加熱空間内に配置し、同加熱空間を常温常圧の状態から約2.5気圧で150~160℃の状態にまで30~40分掛けて昇温し、約2.5気圧で150~160℃の状態を1~3分間維持する。 In the first stevia stem heating process, a specified container that contains stevia stem dispersion after the stevia stem dispersion container placement process is placed in a heating space, and the heating space is heated from room temperature and pressure to 150-160°C at approximately 2.5 atmospheres over a period of 30-40 minutes, and the state of 150-160°C at approximately 2.5 atmospheres is maintained for 1-3 minutes.

第2のステビア茎加熱工程は、第1のステビア茎加熱工程に引き続き、加熱空間を約2気圧で115~125℃の状態にまで3~5分間掛けて降温設定し、約2気圧で115~125℃の状態を20~40分間維持する。 The second stevia stalk heating process follows the first stevia stalk heating process, in which the heating space is cooled to 115-125°C at approximately 2 atmospheres over a period of 3-5 minutes, and then maintained at 115-125°C at approximately 2 atmospheres for 20-40 minutes.

そして、この第1のステビア茎加熱工程と、第2のステビア茎加熱工程とを経た後に、85~95℃まで冷却を行うことにより、ステビア茎分散液中に加熱選抜された乾燥ステビア茎由来の微生物を残存させる。 After the first stevia stem heating process and the second stevia stem heating process, the stevia stem dispersion is cooled to 85-95°C, allowing the heat-selected microorganisms derived from dried stevia stem to remain in the stevia stem dispersion.

ステビア茎抽出液調製工程は、ステビア茎由来微生物選抜工程を経たステビア茎分散液から、固液分離により液相を得る工程である。 The stevia stem extract preparation process is a process in which a liquid phase is obtained by solid-liquid separation from the stevia stem dispersion liquid that has been subjected to the stevia stem-derived microorganism selection process.

具体的には、前述の第2のステビア茎加熱工程に引き続き、85~95℃まで降温させたステビア茎分散液を、少なくとも微生物が液相に移行可能な手段により固液分離して、液相をステビア茎の抽出液として得る。このステビア茎抽出液は、Brix値が2.0~4.0でステビア茎由来の微生物が含まれたものである。 Specifically, following the second stevia stem heating step described above, the stevia stem dispersion liquid is cooled to 85-95°C and then subjected to solid-liquid separation using a means that allows at least the microorganisms to migrate to the liquid phase, and the liquid phase is obtained as a stevia stem extract. This stevia stem extract liquid has a Brix value of 2.0-4.0 and contains microorganisms derived from stevia stem.

抽出液濃縮工程は、ステビア茎抽出液を加熱して煮詰めることにより、所定の濃度まで濃縮することでステビア茎濃縮液を得る工程である。具体的には、ステビア茎抽出液を加熱して煮詰め、常温程度に冷却された状態においてBrix値が4.0~7.0でpHが6.0以下、ORPが10~99mVとなるように濃縮を行う。 The extract concentration process is a process in which the stevia stem extract is heated and boiled down to a specified concentration to obtain a stevia stem concentrate. Specifically, the stevia stem extract is heated and boiled down, and then concentrated so that when cooled to room temperature, the Brix value is 4.0 to 7.0, the pH is 6.0 or less, and the ORP is 10 to 99 mV.

熟成工程は、ステビア茎濃縮液を常温下にて発酵を伴いながら熟成させ、pHが5.0以下でORPが-100mV以下のステビア茎熟成液を得る工程である。 The maturation process involves maturing the stevia stem concentrate at room temperature while fermenting to obtain a stevia stem matured liquid with a pH of 5.0 or less and an ORP of -100mV or less.

このように、ステビア茎分散液調製工程と、ステビア茎分散液容器収容工程と、ステビア茎由来微生物選抜工程と、ステビア茎抽出液調製工程と、抽出液濃縮工程と、熟成工程と、を経ることで、不良発酵防止剤の製造に適したステビア茎の熟成液を得ることができる。 In this way, by going through the stevia stem dispersion preparation process, the stevia stem dispersion container placement process, the stevia stem-derived microorganism selection process, the stevia stem extract preparation process, the extract concentration process, and the maturation process, it is possible to obtain a stevia stem maturation liquid suitable for producing a defective fermentation inhibitor.

そして、前述した静置工程と、容器収容工程と、微生物選抜工程と、固液分離工程と、第1の発酵工程と、第2の発酵工程とを経て製造された液を鶏糞発酵微生物発酵液として採用すれば、鶏糞の発酵をより堅実に行うことができる。 Furthermore, if the liquid produced through the above-mentioned settling process, container placement process, microorganism selection process, solid-liquid separation process, first fermentation process, and second fermentation process is used as a chicken manure fermentation microorganism fermentation liquid, the fermentation of chicken manure can be carried out more reliably.

なお、この鶏糞発酵微生物発酵液は上述した方法によって得られるものではあるが、これは当該鶏糞発酵微生物発酵液の製造方法を限定しているものではなく、鶏糞発酵微生物発酵液を、静置工程と容器収容工程と微生物選抜工程と固液分離工程と第1の発酵工程と第2の発酵工程との製造方法によって特定しているものである。 Although this chicken manure fermentation microorganism fermentation liquid is obtained by the method described above, this does not limit the manufacturing method of the chicken manure fermentation microorganism fermentation liquid, but specifies the manufacturing method of the chicken manure fermentation microorganism fermentation liquid by the settling step, container placement step, microorganism selection step, solid-liquid separation step, first fermentation step, and second fermentation step.

一般に、植物粉末や米ぬか、おから、汽水の如き天然物には、他の天然物と同様に、様々な成分や微生物が複雑な状態や配合比で含まれている。そして、上述のスクリーニング環境下で、他の微生物が利用し得なかった成分を利用できたり、ある微生物の代謝産物に利用価値を見出しうる所定の微生物が選抜されたり、更にはこれら原料を構成する成分の存在により好適な発酵が可能な鶏糞発酵微生物発酵液として機能しうるものと考えられる。 In general, natural products such as plant powders, rice bran, soybean pulp, and brackish water contain various components and microorganisms in complex states and ratios, just like other natural products. In the above-mentioned screening environment, it is believed that certain microorganisms can be selected that can utilize components that other microorganisms cannot utilize, or that can find value in the metabolic products of certain microorganisms, and furthermore, that the presence of the components that make up these raw materials can function as a chicken manure fermentation microbial fermentation liquid that can perform suitable fermentation.

しかしながら、このような底質改善を生起する微生物叢を構成する個々の菌を同定したりその菌数を定量したりすることや、各原料に由来する成分の種類や濃度を規定したりすることは、製造過程での微生物による発酵代謝やその産物まで勘案すると、所定のパラメーター等で直接特定することは、不可能であるか又はおよそ実際的でない。 However, when taking into account the fermentation metabolism of microorganisms during the manufacturing process and their products, it is impossible or almost impractical to directly identify the individual bacteria that make up the microbial flora that causes this type of bottom sediment improvement, quantify the number of bacteria, or specify the type and concentration of components derived from each raw material using specific parameters.

従って、鶏糞発酵微生物発酵液を製造方法で特定したのは、鶏糞発酵微生物発酵液は製造方法によってしか特定できないためである。また、本実施形態に係る海域施肥材の構成要素としての鶏糞発酵微生物発酵液についても同様である。 Therefore, the chicken manure fermentation microorganism fermentation liquid was specified by the manufacturing method because the chicken manure fermentation microorganism fermentation liquid can only be specified by the manufacturing method. The same applies to the chicken manure fermentation microorganism fermentation liquid as a component of the marine fertilizer material according to this embodiment.

また、本実施形態に係る海域施肥材の原料である発酵鶏糞についても同様であり、被発酵混合物を調製する工程と、発酵を助長する工程と、切り返し工程と、繰返工程と、発酵鶏糞生成工程と、を経て製造したものとして説明したが、これは発酵鶏糞の製造方法、ひいては海域施肥材の製造方法を限定しているものではなく、発酵鶏糞を、被発酵混合物を調製する工程と、発酵を助長する工程と、切り返し工程と、繰返工程と、発酵鶏糞生成工程との製造方法によって特定しているものであって、このような発酵鶏糞内の微生物叢を構成する個々の菌を同定したりその菌数を定量したりすることや、各原料に由来する成分の種類や濃度を規定したりすることは、製造過程での微生物による発酵代謝やその産物まで勘案すると、所定のパラメーター等で直接特定することは、不可能であるか又はおよそ実際的でない。すなわち、発酵鶏糞を製造方法で特定したのも、製造方法によってしか特定できないためである。但し、出願人が本願を権利化するに際し、鶏糞発酵微生物発酵液や発酵鶏糞等の製造方法の一部又は全部について意図的に限定する解釈を行うことを妨げるものではない。 The same is true for the fermented chicken manure, which is the raw material for the marine fertilizer according to this embodiment. It has been described as being produced through the steps of preparing a fermented mixture, promoting fermentation, turning, repeating, and producing fermented chicken manure. However, this does not limit the method for producing fermented chicken manure, or the method for producing marine fertilizer. The fermented chicken manure is specified by the method for producing the steps of preparing a fermented mixture, promoting fermentation, turning, repeating, and producing fermented chicken manure. Identifying the individual bacteria that make up the microflora in the fermented chicken manure, quantifying the number of bacteria, and specifying the types and concentrations of components derived from each raw material are impossible or almost impractical to directly specify using predetermined parameters, etc., taking into account the fermentation metabolism by microorganisms during the production process and their products. In other words, the fermented chicken manure is specified by the production method because it can only be specified by the production method. However, this does not prevent the applicant from intentionally interpreting the invention in a way that limits some or all of the manufacturing method for the chicken manure fermentation microorganism fermentation liquid, fermented chicken manure, etc., when granting the patent for this application.

また、上述してきた本実施形態に係る海域施肥材の各構成についての説明は、本実施形態に係る海域施肥材の製造方法の各構成についての説明として解することが可能である。 The above explanation of each component of the marine fertilization material according to this embodiment can be interpreted as an explanation of each component of the manufacturing method of the marine fertilization material according to this embodiment.

すなわち、本実施形態に係る海域施肥材の製造方法では、12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水との混合材料を高さ10~30cm、幅15~30cmの柱状に圧縮成形することとしており、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現でき、更には二枚貝の成長と生残を効果的に上げることができる海域施肥材を製造することができる。 In other words, in the manufacturing method of marine fertilizer according to this embodiment, a mixture of 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water that will result in a moisture content of the marine fertilizer of 45 to 60% by weight is compressed and molded into a column shape 10 to 30 cm in height and 15 to 30 cm in width, and a marine fertilizer can be manufactured that is a highly sustainable organic fertilizer that is mainly composed of chicken manure-derived materials, can dissolve nutrients suitable for the growth of algae that serves as food for herbivorous bivalve mollusks, and can effectively increase the growth and survival of bivalve mollusks.

また、本願は、本実施形態に係る海域施肥材の設置方法についても提供する。本願設置方法は、上述の海域施肥材や海域施肥材の製造方法にて製造された海域施肥材の設置方法であって、海域施肥材の高さと同程度の穴を干潟に形成して設置する工程と、形成した穴に海域施肥材を配置したのち、同海域施肥材の上部をわずかの砂で被覆する工程と、を有することとしている。 The present application also provides a method for installing the marine fertilization material according to this embodiment. The installation method of the present application is a method for installing the marine fertilization material or the marine fertilization material manufactured by the manufacturing method of the marine fertilization material described above, and includes a step of forming a hole of approximately the same height as the marine fertilization material in the tidal flat and installing the material, and a step of placing the marine fertilization material in the formed hole and then covering the top of the marine fertilization material with a small amount of sand.

このような構成とすることにより、海域施肥材を水中に設置する際に、同海域施肥材の表面へのとくに大型藻類の付着を防止し、施肥材の構成成分の溶出の円滑化を図ることが可能となる。 This configuration makes it possible to prevent adhesion of large algae, in particular, to the surface of the marine fertilization material when it is placed underwater, and to facilitate the elution of the constituent components of the fertilization material.

従って、海域施肥材の設置が簡便でありながら、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現可能な海域施肥材としての効果を良好に発揮させることができる。 This marine fertilizer is easy to install, is a highly sustainable organic fertilizer, and uses chicken manure as its main component, and is effective as a marine fertilizer that can dissolve nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks.

以下、本実施形態に係る海域施肥材や同製造方法、設置方法について製造過程や試験結果等を交えつつ、更に説明する。 The marine fertilizer material, manufacturing method, and installation method according to this embodiment will be further explained below, including the manufacturing process and test results.

〔1.鶏糞発酵微生物のスクリーニング〕
20L容量のステンレス容器(直径32cmで高さ38cm)内に、0.85kgの乾燥ステビア茎粉末と、0.85kgの米ぬか粉末と、0.85kgの乾燥おから粉末とを投入し、更に山口県の阿武川河口の汽水域(塩分濃度が0.8~1.0%程度の領域)にて採取された汽水17kgを添加して攪拌混合したものを数バッチ調製し、常温で一晩(約15~17時間)静置した(静置工程)。この静置した混合物の微生物検査の結果、検出された幾つかの微生物の中から、少なくともLactobacillus buchneriの存在が確認された。
[1. Screening of chicken manure fermentation microorganisms]
In a 20L stainless steel container (diameter 32cm, height 38cm), 0.85kg of dried stevia stem powder, 0.85kg of rice bran powder, and 0.85kg of dried soybean pulp powder were added, and 17kg of brackish water collected from the Abu River estuary in Yamaguchi Prefecture (area with a salinity of about 0.8-1.0%) was added, stirred, and mixed to prepare several batches, which were then left to stand overnight (about 15-17 hours) at room temperature (standing process). A microbial test of the mixture that had been left to stand confirmed the presence of at least Lactobacillus buchneri among several microorganisms detected.

また、採取した汽水について別途微生物検査を行ったところ、汽水中には150cfu/mlの濃度で耐塩性酵母群が含まれていることが確認された。 In addition, a separate microbial test was conducted on the collected brackish water, confirming that it contained salt-tolerant yeasts at a concentration of 150 cfu/ml.

次いで、約20.31L容量の蓋付きステンレス容器P1(内径28cmで高さ33cmの円筒状)内に静置工程を経た混合液を20L収容し、容器内に弱殺菌領域を形成させた(容器収容工程)。また、同様に、約21.04L容量の蓋付きステンレス容器Q1(内径20cmで高さ67cmの円筒状)に、静置工程を経た混合液を20.41L収容し、ステンレス容器Q1内に収容された混合液の収容形状を直径20cmで高さ65cmの円柱状として弱殺菌領域を形成した。併せて、約32.67L容量の蓋付きステンレス容器R1(内径34cmで高さ36cmの円筒状)に、静置工程を経た混合液を30.85L収容し、ステンレス容器R1内に収容された混合液の収容形状を直径34cmで高さ34cmの円柱状として弱殺菌領域を形成した。 Next, 20 L of the mixture that had undergone the standing process was placed in a lidded stainless steel container P1 (cylindrical with an inner diameter of 28 cm and a height of 33 cm) with a capacity of approximately 20.31 L, and a weak sterilization area was formed in the container (container placement process). Similarly, 20.41 L of the mixture that had undergone the standing process was placed in a lidded stainless steel container Q1 (cylindrical with an inner diameter of 20 cm and a height of 67 cm) with a capacity of approximately 21.04 L, and the shape of the mixture placed in the stainless steel container Q1 was set to a cylindrical shape with a diameter of 20 cm and a height of 65 cm, forming a weak sterilization area. In addition, 30.85 L of the mixture that had undergone the standing process was placed in a lidded stainless steel container R1 (cylindrical with an inner diameter of 34 cm and a height of 36 cm) with a capacity of approximately 32.67 L, and the shape of the mixture placed in the stainless steel container R1 was set to a cylindrical shape with a diameter of 34 cm and a height of 34 cm, forming a weak sterilization area.

次に、加圧クッカー内に、混合液を各ステンレス容器P1,Q1,R1ごと収納し、約2.5気圧で150~160℃の状態にまで45~60分掛けて昇温し、約2.5気圧で150~160℃の状態を1~3分間維持させた(第1の加熱工程)。 Next, the mixed liquid was placed in each of the stainless steel containers P1, Q1, and R1 in a pressure cooker, and the temperature was raised to 150-160°C at approximately 2.5 atmospheres over 45-60 minutes, and the state of 150-160°C at approximately 2.5 atmospheres was maintained for 1-3 minutes (first heating step).

次に、引き続いて約2気圧で115~125℃の状態にまで3~5分間掛けて降温し、約2気圧で115~125℃の状態を20~40分間維持させた(第2の加熱工程)。 Next, the temperature was lowered to 115-125°C at approximately 2 atm over a period of 3-5 minutes, and the temperature was maintained at 115-125°C at approximately 2 atm for 20-40 minutes (second heating step).

次に、加圧クッカーの加熱スイッチを切り、加圧クッカーの内部温度が常温常圧の状態となるまで24~30時間掛けて降温させた(降温工程)。 Next, the heating switch of the pressure cooker was turned off, and the temperature inside the pressure cooker was allowed to drop to room temperature and pressure over a period of 24 to 30 hours (temperature drop process).

そして、加圧クッカーの蓋を開けて、各ステンレス容器P1,Q1,R1内に鶏糞発酵微生物のスクリーニングが行われた混合液を得た。この混合液の微生物検査の結果、検出された幾つかの微生物の中から、少なくともLactobacillus buchneriの存在が確認された。 Then, the lid of the pressure cooker was opened, and a mixture was obtained in each of the stainless steel containers P1, Q1, and R1, in which the chicken manure fermentation microorganisms had been screened. As a result of the microbial testing of this mixture, the presence of at least Lactobacillus buchneri was confirmed among the several microorganisms detected.

〔2.ステビア茎の熟成液の調製〕
まず、所定の容器に1kgの乾燥ステビア茎粉末に対して10±2kgの水を添加して満遍なく混合し、ステビア茎の分散液を調製した(ステビア茎分散液調製工程)。なお、このステビア茎の分散液は数バッチ調製した。
2. Preparation of stevia stem ripening liquid
First, 10±2 kg of water was added to 1 kg of dried stevia stem powder in a specified container and mixed thoroughly to prepare a stevia stem dispersion (stevia stem dispersion preparation step). Note that this stevia stem dispersion was prepared in several batches.

次に、約12.27L容量の蓋付きステンレス容器P2(内径25cmで高さ25cm)内に、ステビア茎分散液調製工程にて調製したステビア茎分散液12Lを収容し、容器内に収容したステビア茎分散液に弱殺菌領域を形成させた(ステビア茎分散液容器収容工程)。また、同様に、約21.04L容量の蓋付きステンレス容器Q1(内径20cmで高さ67cmの円筒状)に、ステビア茎分散液調製工程にて調製したステビア茎分散液を12L収容し、ステンレス容器Q1内に収容されたステビア茎分散液の収容形状を直径20cmで高さ38cmの円柱状として弱殺菌領域を形成した。併せて、約32.67L容量の蓋付きステンレス容器R1(内径34cmで高さ36cmの円筒状)に、ステビア茎分散液調製工程にて調製したステビア茎分散液を30.85L収容し、ステンレス容器R1内に収容されたステビア茎分散液の収容形状を直径34cmで高さ34cmの円柱状として弱殺菌領域を形成した。 Next, 12 L of the stevia stem dispersion liquid prepared in the stevia stem dispersion liquid preparation process was placed in a lidded stainless steel container P2 (inner diameter 25 cm, height 25 cm) with a capacity of approximately 12.27 L, and a weak sterilization area was formed in the stevia stem dispersion liquid placed in the container (stevia stem dispersion liquid container placement process). Similarly, 12 L of the stevia stem dispersion liquid prepared in the stevia stem dispersion liquid preparation process was placed in a lidded stainless steel container Q1 (cylindrical shape with an inner diameter of 20 cm and a height of 67 cm) with a capacity of approximately 21.04 L, and the shape of the stevia stem dispersion liquid placed in the stainless steel container Q1 was made cylindrical with a diameter of 20 cm and a height of 38 cm, forming a weak sterilization area. In addition, 30.85 L of the stevia stem dispersion liquid prepared in the stevia stem dispersion liquid preparation process was placed in a lidded stainless steel container R1 (cylindrical with an inner diameter of 34 cm and a height of 36 cm) with a capacity of approximately 32.67 L, and the shape of the stevia stem dispersion liquid contained in the stainless steel container R1 was made cylindrical with a diameter of 34 cm and a height of 34 cm to form a weak sterilization area.

次に、加圧クッカー内に、ステビア茎分散液をステンレス容器P2,Q1,R1ごと収納し、約2.5気圧で150~160℃の状態にまで30~40分掛けて昇温し、約2.5気圧で150~160℃の状態を1~3分間維持させた(第1のステビア茎加熱工程)。 Next, the stevia stem dispersion liquid was placed in the stainless steel containers P2, Q1, and R1 in a pressure cooker and heated to 150-160°C at approximately 2.5 atmospheres over 30-40 minutes, and then maintained at 150-160°C at approximately 2.5 atmospheres for 1-3 minutes (first stevia stem heating process).

次に、引き続いて約2気圧で115~125℃の状態にまで3~5分間掛けて降温設定し、約2気圧で115~125℃の状態を20~40分間維持させた(第2のステビア茎加熱工程)。 Next, the temperature was lowered to 115-125°C at approximately 2 atm over a period of 3-5 minutes, and the temperature was maintained at 115-125°C at approximately 2 atm for 20-40 minutes (second stevia stalk heating process).

次に、加圧クッカーの加熱を終了し、加圧クッカーの内部が略常圧(開蓋可能な圧力)となり約85~95℃となったのを見計らって、ステビア茎分散液を収容したステンレス容器P2,Q1,R1を加圧クッカーから取出し、綿製の布袋内にステビア茎分散液を移した。 Next, the heating of the pressure cooker was stopped, and when the inside of the pressure cooker reached approximately normal pressure (a pressure at which the lid could be opened) and the temperature reached approximately 85-95°C, the stainless steel containers P2, Q1, and R1 containing the stevia stem dispersion were removed from the pressure cooker, and the stevia stem dispersion was transferred into a cotton cloth bag.

ステビア茎分散液を収容した布袋は、熱い状態のまま脱水装置に供し、固液分離を行ってステビア茎抽出液を得た(ステビア茎抽出液調製工程)。このステビア茎抽出液は、Brix値が2.0~4.0であり、別途行った微生物検査によりステビア茎由来の微生物であるLactobacillus属の微生物がステンレス容器P2,Q1,R1のいずれにも含まれていることが確認された。 The cloth bag containing the stevia stem dispersion was placed in a dehydrator while still hot, and solid-liquid separation was carried out to obtain a stevia stem extract (stevia stem extract preparation process). This stevia stem extract had a Brix value of 2.0 to 4.0, and a separate microbial test confirmed that the genus Lactobacillus, a microorganism derived from stevia stem, was contained in all of the stainless steel containers P2, Q1, and R1.

次に、得られたステビア茎抽出液を耐熱性の所定容器にそれぞれ収容し、ガスコンロ上に載置して4~5時間程度加熱しつつ煮詰めることでステビア茎濃縮液の調製を行った(抽出液濃縮工程)。その後、加熱を終了し、常温まで放置冷却したした後にステビア茎濃縮液について理化学検査を行ったところ、Brix値が4.0~7.0でpHが6.0以下、ORPが10~99mVであることが確認された。 Next, the obtained stevia stem extract was placed in a heat-resistant container and placed on a gas stove for about 4 to 5 hours to prepare a stevia stem concentrate (extract concentration process). After that, the heating was stopped and the stevia stem concentrate was left to cool to room temperature. A physical and chemical test was then performed on the stevia stem concentrate, which confirmed that the Brix value was 4.0 to 7.0, the pH was 6.0 or less, and the ORP was 10 to 99 mV.

次に、得られたステビア茎濃縮液をステンレス製のフック付の発酵熟成缶(12L容量)に収容し、常温環境下にて静置して熟成を行った(熟成工程)。熟成中は、ステンレス容器P2,Q1,R1のいずれのステビア茎濃縮液からも発酵臭を伴うガスの発生があり、ステンレス容器P2,Q1,R1の容器形状の差異に拘わらず略同程度の発酵を伴っていることが確認された。 Next, the obtained stevia stem concentrate was placed in a stainless steel fermentation and maturation can (12 L capacity) with a hook and left to stand at room temperature for maturation (maturation process). During maturation, gas accompanied by a fermentation odor was generated from each of the stevia stem concentrates in the stainless steel containers P2, Q1, and R1, and it was confirmed that the fermentation occurred to approximately the same extent regardless of the difference in the container shape of the stainless steel containers P2, Q1, and R1.

そして、熟成中のステビア茎濃縮液のpHが5.0以下で、且つ、ORPが-100mV以下となった時点でステビア茎熟成液とした。また、この時点においてもステンレス容器P2,Q1,R1の容器形状に由来する異常発酵などの差異は認められず、この後の実験においてステビア茎熟成液は、いずれも同じものとして扱うこととした。 The stevia stem concentrate was considered to be matured stevia stem liquid when its pH was below 5.0 and its ORP was below -100mV during maturation. Even at this point, no differences such as abnormal fermentation due to the shape of the stainless steel containers P2, Q1, and R1 were observed, so in subsequent experiments, all of the matured stevia stem liquids were treated as the same.

〔3.鶏糞発酵微生物発酵液の調製〕
前述の〔1.鶏糞発酵微生物のスクリーニング〕により降温工程を経て鶏糞発酵微生物のスクリーニングが行われたステンレス容器P1,Q1,R1中の混合液をそれぞれ別個に綿製の布袋内に収容し、この布袋を脱水装置に供して固液分離を行って微生物含有液を得た(固液分離工程)。
3. Preparation of chicken manure fermentation microbial fermentation liquid
The mixed liquids in the stainless steel containers P1, Q1, and R1, which had been subjected to the temperature-lowering process and screening of poultry manure fermentation microorganisms as described above in [1. Screening of poultry manure fermentation microorganisms], were each placed separately in cotton cloth bags, and these cloth bags were subjected to a dehydrator to perform solid-liquid separation to obtain a microorganism-containing liquid (solid-liquid separation process).

次に、フック付の発酵熟成缶(12L容量)に固液分離した微生物含有液約9kgをステンレス容器P1,Q1,R1別に入れ、0.1kgのメープルシロップを糖源としてそれぞれ添加して均一に攪拌し、常温常圧で大凡20~30日間静置して発酵を行わせた(第1の発酵工程)。 Next, about 9 kg of the solid-liquid separated microorganism-containing liquid was placed in stainless steel containers P1, Q1, and R1, each of which was placed in a fermentation/aging can (12 L capacity) with a hook, and 0.1 kg of maple syrup was added to each as a sugar source, stirred uniformly, and left to stand at room temperature and pressure for approximately 20 to 30 days to allow fermentation to occur (first fermentation process).

この第1の発酵工程の初期段階では、微生物含有液の液表面に上澄みが生成するが、これは発明者らの経験上、発酵を緩慢化させるため数日毎に取り除いた。また、この初期段階を経過すると、微生物含有液はあたかもビールのような感じで泡立ち初め、微生物により発酵が行われていることが確認された。 In the initial stage of this first fermentation process, a supernatant is formed on the surface of the microorganism-containing liquid, but based on the inventors' experience, this is removed every few days to slow down the fermentation. In addition, after this initial stage, the microorganism-containing liquid begins to foam like beer, confirming that fermentation is taking place by the microorganisms.

そして、微生物含有液のpHが4.5以下で、且つ、酸化還元電位が-100mV以下となった時点で第1の発酵工程を終了した。なお、この時点においてステンレス容器P1,Q1,R1の間における容器形状の差異に由来する異常発酵などの違いは確認されなかった。 The first fermentation process was terminated when the pH of the microorganism-containing liquid was 4.5 or less and the redox potential was -100 mV or less. At this point, no differences such as abnormal fermentation due to differences in the container shapes were observed between the stainless steel containers P1, Q1, and R1.

次に、第1の発酵工程を経た微生物含有液に対し、前述の〔2.ステビア茎の熟成液の調製〕にて得られたステビア茎熟成液を添加して均一に攪拌し、常温常圧で大凡20~25日間静置して発酵を行わせた(第2の発酵工程)。 Next, the stevia stem matured liquid obtained in the above [2. Preparation of stevia stem matured liquid] was added to the microorganism-containing liquid that had been through the first fermentation process, and the mixture was stirred uniformly and left to stand at room temperature and pressure for approximately 20 to 25 days to allow fermentation to occur (second fermentation process).

具体的には、10L容量の二次発酵缶に、0.75kgの第1の発酵工程を経たステンレス容器P1,Q1,R1いずれかの微生物含有液と、0.75kgのステビア茎熟成液とを収容し、更に水を加えて10kgとし均一に攪拌することで、第2の発酵工程に供する被発酵液の調製を行った。なお、被発酵液に対しては、必要に応じて0.75kg程度の糖源を更に添加しても良く、例えば、オリゴ糖、より好ましくはテンサイ糖を添加することができる。 Specifically, 0.75 kg of the microorganism-containing liquid from stainless steel container P1, Q1, or R1 that had undergone the first fermentation step and 0.75 kg of stevia stalk aged liquid were placed in a 10 L secondary fermentation can, and water was added to bring the total weight to 10 kg, followed by uniform stirring to prepare the fermented liquid to be subjected to the second fermentation step. If necessary, about 0.75 kg of a sugar source may be further added to the fermented liquid, for example, oligosaccharides, more preferably sugar beet sugar, may be added.

そして、pHが3.1以下となるまで発酵させた時点で第2の発酵工程を終了し、得られた発酵液を鶏糞発酵微生物発酵液とした。また、この時点においてもステンレス容器P1,Q1,R1の容器形状に由来する異常発酵などの差異は認められず、この後の試験において鶏糞発酵微生物発酵液は、いずれも同じものとして扱うこととした。鶏糞発酵微生物発酵液中のChromatium属に属する光合成細菌群の数は20cfu/ml以下であった。また、耐塩性酵母群の菌数は1,2×106cfu/mlであった。 The second fermentation step was terminated when the pH reached 3.1 or less, and the resulting fermentation liquid was designated as a chicken manure fermentation microorganism fermentation liquid. At this stage, no differences such as abnormal fermentation due to the shape of the stainless steel containers P1, Q1, and R1 were observed, and all chicken manure fermentation microorganism fermentation liquids were treated as the same in the subsequent tests. The number of photosynthetic bacteria belonging to the genus Chromatium in the chicken manure fermentation microorganism fermentation liquid was 20 cfu/ml or less. The number of salt-tolerant yeasts was 1.2 x 106 cfu/ml.

〔4.発酵鶏糞の製造〕
ブロイラーの鶏舎より排出された10トンの鶏糞(水分40%程度)に対し、希釈した鶏糞発酵微生物発酵液5トンを添加して攪拌混合し、鶏糞発酵微生物発酵液が添加された鶏糞である15トンの被発酵混合物(水分60±5%程度)を調製した(被発酵混合物調製工程)。なお、ブロイラーの鶏舎より排出された鶏糞は敷材が含まれており、水分含量が70%の生鶏糞に対し該敷材が水分調整材となって水分が40%に調整されている。また、希釈した鶏糞発酵微生物発酵液は、25kgの鶏糞発酵微生物発酵液を水で200倍希釈して5トンに調製したものである。
[4. Production of fermented chicken manure]
Five tons of diluted chicken manure fermentation microorganism fermentation liquid was added to 10 tons of chicken manure (about 40% moisture) discharged from a broiler chicken house, and the mixture was stirred and mixed to prepare 15 tons of a fermented mixture (about 60±5% moisture) of chicken manure to which chicken manure fermentation microorganism fermentation liquid was added (fermented mixture preparation process). Note that the chicken manure discharged from the broiler chicken house contains bedding, and the bedding acts as a moisture regulator to adjust the moisture content to 40% for the raw chicken manure with a moisture content of 70%. The diluted chicken manure fermentation microorganism fermentation liquid was prepared by diluting 25 kg of chicken manure fermentation microorganism fermentation liquid 200 times with water to prepare 5 tons.

次に、屋根が配されたコンクリート製の発酵ヤード内にて、調製した15トンの被発酵混合物を高さ凡そ1.8mに堆積させ(発酵助長工程)、この状態で放置したところ4~5日程度で被発酵混合物の温度上昇が認められた。 Next, 15 tons of the prepared fermentation mixture was piled up to a height of approximately 1.8 m in a roofed concrete fermentation yard (fermentation promotion process), and when it was left in this state, a rise in the temperature of the fermentation mixture was observed within about 4 to 5 days.

堆積した被発酵混合物の温度測定を引き続き毎日行い、被発酵混合物の温度が70℃以上となった際に、80℃に達する前に切り返しを行い、再び被発酵混合物を堆積させることで切り返し工程を実施した。 The temperature of the piled fermented mixture was continued to be measured daily, and when the temperature of the fermented mixture reached 70°C or higher, it was turned over before it reached 80°C, and the turning process was carried out by piling the fermented mixture again.

そしてこの切り返し工程を5回ほど行って、昇温と切り返しを繰り返すことで、被発酵混合物の水分含量を35%以下、ここでは33%程度まで低下させた(繰返工程)。なお、この被発酵混合物は、水分を約40%程度まで与えたとしても、70℃以上にまで昇温することはなく、微生物による発酵が相当に進んでいることが確認された。 This process of turning the mixture over and over was repeated about five times, lowering the moisture content of the fermented mixture to 35% or less, in this case to about 33% (repeated process). Furthermore, even when the moisture content of this fermented mixture was increased to about 40%, it was not heated to above 70°C, confirming that fermentation by microorganisms had progressed considerably.

次に、繰返工程を経た被発酵混合物に対し、ここでは追加発酵工程に供することで発酵鶏糞生成工程を行った。 Next, the fermented mixture that had undergone the repeating process was subjected to an additional fermentation process to produce fermented chicken manure.

発酵ヤードのコンクリート壁にもたれかけるように高く(例えば、2m強)堆積させ、自重で圧縮しながら、一月に1~2回切り返しつつ、水分含量が30%を下回る程度まで熟成を行った。 The lees were piled high (e.g., just over 2m) against the concrete wall of the fermentation yard, compressed by their own weight, and turned over once or twice a month while they were aged until the moisture content was below 30%.

被発酵混合物は、昇温度合いはやや鈍いものの、更に発酵が進行した。切り返しを行っても水蒸気が出なくなる程度まで発酵させたところ、水分が20%以下となり、このときの窒素分が2.8%以上、リン酸が3.8%以上、カリウムが3.0%以上となり、これを発酵鶏糞とした。 The fermented mixture continued to ferment, although the temperature rise was somewhat slow. When it was allowed to ferment until steam no longer came out even when it was turned over, the moisture content was below 20%, the nitrogen content was over 2.8%, the phosphoric acid content was over 3.8%, and the potassium content was over 3.0%, and this was called fermented chicken manure.

〔5.粒状鉄〕
本実施形態に係る海域施肥材の製造原料用の粒状鉄として、製鉄会社より入手した鉄鋼スラグを採用した。鉄鋼スラグは直径が3~10mm程度の粒状を呈していた。
[5. Granular iron]
As the granular iron for the raw material for manufacturing the marine fertilizer according to this embodiment, steel slag obtained from a steel company was used. The steel slag had a granular shape with a diameter of about 3 to 10 mm.

〔6.酸化マグネシウム〕
市販されている粉末状の酸化マグネシウムを、本実施形態に係る海域施肥材の製造原料用の酸化マグネシウムとして使用した。
[6. Magnesium oxide]
Commercially available powdered magnesium oxide was used as the magnesium oxide for the raw material for producing the marine fertilizer material according to this embodiment.

〔7.海域施肥材の製造(原料の混合及び成形)〕
次に、上述の各原料を混合し、加圧成形することで海域施肥材の製造を行った。具体的には、12重量部の発酵鶏糞と、4重量部の粒状鉄と、4重量部の酸化マグネシウムとを混合し、更に同混合物の水分含量が45~60重量%となる量の水分を添加して混合を行うことにより水分調整混合物の調製を行った。
[7. Manufacturing of marine fertilizers (mixing and molding of raw materials)]
Next, the above-mentioned raw materials were mixed and pressure-molded to produce a marine fertilizer. Specifically, 12 parts by weight of fermented chicken manure, 4 parts by weight of granular iron, and 4 parts by weight of magnesium oxide were mixed, and water was added in an amount to make the water content of the mixture 45 to 60% by weight, and the mixture was mixed to prepare a moisture-adjusted mixture.

次いで、プレス機を用いて水分調整混合物に対し0.4平方メートルあたり500kgfの圧力で3回転圧プレスを行い、高さ20cm、直径25cm(面積/体積比=0.24)の円柱状に高密度成形された本実施形態に係る海域施肥材Xを製造した。 Next, the moisture-adjusted mixture was pressed three times using a press at a pressure of 500 kgf per 0.4 square meters to produce marine fertilizer material X according to this embodiment, which was densely molded into a cylindrical shape with a height of 20 cm and a diameter of 25 cm (area/volume ratio = 0.24).

〔8.鉄鋼スラグの量の違いによるFe溶出量の確認試験〕
次に、海域施肥材中に含まれる鉄鋼スラグの量の違いにより、Feの溶出量がどのように変化するかについて確認を行った。
[8. Test to confirm the amount of Fe eluted due to different amounts of steel slag]
Next, we confirmed how the amount of Fe elution changes depending on the amount of steel slag contained in the marine fertilizer.

具体的には、前述の〔7.海域施肥材の製造(原料の混合及び成形)〕の方法に従い、鉄鋼スラグの配合量が異なる3種類の海域施肥材を製造した。製造した海域施肥材は、発酵鶏糞:鉄鋼スラグ:酸化マグネシウム=12重量部:2重量部:4重量部としたもの(海域施肥材Xa)、同比率を12:4:4としたもの(海域施肥材Xb)、同比率を12:6:4としたもの(海域施肥材Xc)の3つである。原料として使用した発酵鶏糞と鉄鋼スラグと酸化マグネシウムの合計重量に対する鉄鋼スラグの割合は、海域施肥材Xaは11%、海域施肥材Xbは20%、海域施肥材Xcは27%である。 Specifically, three types of marine fertilizers with different amounts of steel slag were manufactured according to the method described above in [7. Manufacturing marine fertilizers (mixing and molding of raw materials)]. The marine fertilizers manufactured were one with a ratio of fermented chicken manure:steel slag:magnesium oxide = 12 parts by weight:2 parts by weight:4 parts by weight (marine fertilizer Xa), one with a ratio of 12:4:4 (marine fertilizer Xb), and one with a ratio of 12:6:4 (marine fertilizer Xc). The ratio of steel slag to the total weight of the fermented chicken manure, steel slag, and magnesium oxide used as raw materials was 11% for marine fertilizer Xa, 20% for marine fertilizer Xb, and 27% for marine fertilizer Xc.

実験は、100Lの海水を入れた3つの水槽の底部に、高さ20cm、直径25cmとした海域施肥材Xa~Xcをぞれぞれ配置し、リンに対する鉄の溶出モル比を実験開始3日後と7日後に算出することで行った。その結果を図1に示す。 The experiment was carried out by placing marine fertilizer materials Xa to Xc, each 20 cm high and 25 cm in diameter, at the bottom of three tanks containing 100 L of seawater, and calculating the molar ratio of iron to phosphorus dissolved 3 and 7 days after the start of the experiment. The results are shown in Figure 1.

図1からも分かるように、12重量部の発酵鶏糞と、鉄鋼スラグと、4重量部の酸化マグネシウムと、水分含量が45~60重量%となる量の水とを含む海域施肥材は、鉄鋼スラグの割合を2~6重量部の範囲内で変化させた場合であっても、Fe/P=0.001~0.1の溶出を実現でき、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出が可能であることが示された。 As can be seen from Figure 1, the marine fertilizer material, which contains 12 parts by weight of fermented chicken manure, steel slag, 4 parts by weight of magnesium oxide, and water in an amount that results in a moisture content of 45 to 60% by weight, can achieve an Fe/P ratio of 0.001 to 0.1 even when the proportion of steel slag is changed within the range of 2 to 6 parts by weight, demonstrating that it is possible to dissolve nutrients suitable for the growth of algae, which serves as food for herbivorous bivalve mollusks.

〔9.MgO量の違いによる溶出成分確認試験〕
次に、酸化マグネシウムの添加量の違いによる無機窒素分やリン酸の溶出速度の違いについて検討を行った。実験は、海域施肥材(大豆程度の小粒に成形したもの)2gを円筒状半透膜チューブに収容し、内部に適量の滅菌ろ過人工海水を入れ、空気を抜いて両端を閉塞して溶出検体を作成した。
[9. Test to confirm eluted components due to differences in MgO content]
Next, we investigated the effect of different amounts of magnesium oxide on the elution rates of inorganic nitrogen and phosphoric acid. In the experiment, 2 g of marine fertilizer (molded into small grains the size of soybeans) was placed in a cylindrical semipermeable membrane tube, and an appropriate amount of sterilized filtered artificial seawater was added. The air was removed and both ends were blocked to create an elution sample.

次いで、400mLの人工海水を収容した500mL容量の容器内に溶出検体を浮遊させ、試験開始から3日経過後と7日経過後に、容器内の人工海水への無機窒素分やリン酸の溶出割合を測定した。 Next, the eluted samples were suspended in a 500 mL container containing 400 mL of artificial seawater, and the percentage of inorganic nitrogen and phosphate eluted into the artificial seawater in the container was measured three and seven days after the start of the test.

試験は、酸化マグネシウムの添加量を違えた7種類の海域施肥材を対象とした。具体的には、発酵鶏糞:鉄鋼スラグ:酸化マグネシウム=12重量部:4重量部:0重量部(無添加)としたもの(海域施肥材Xd)、同比率を12:4:1としたもの(海域施肥材Xe)、同比率を12:6:2としたもの(海域施肥材Xf)、同比率を12:6:3としたもの(海域施肥材Xg)、同比率を12:6:4としたもの(海域施肥材Xh)、同比率を12:6:6としたもの(海域施肥材Xi)、同比率を12:6:10としたもの(海域施肥材Xj)の7つである。原料として使用した発酵鶏糞と鉄鋼スラグと酸化マグネシウムの合計重量に対する酸化マグネシウムの割合は、海域施肥材Xdは0%、海域施肥材Xeは5%、海域施肥材Xfは11%、海域施肥材Xgは15%、海域施肥材Xhは20%、海域施肥材Xiは27%、海域施肥材Xjは38%である。その結果を図2に示す。 The test involved seven types of marine fertilizer materials with different amounts of magnesium oxide added. Specifically, the seven materials were: fermented chicken manure:steel slag:magnesium oxide = 12 parts by weight:4 parts by weight:0 parts by weight (no additives) (marine fertilizer material Xd), a ratio of 12:4:1 (marine fertilizer material Xe), a ratio of 12:6:2 (marine fertilizer material Xf), a ratio of 12:6:3 (marine fertilizer material Xg), a ratio of 12:6:4 (marine fertilizer material Xh), a ratio of 12:6:6 (marine fertilizer material Xi), and a ratio of 12:6:10 (marine fertilizer material Xj). The percentage of magnesium oxide relative to the total weight of fermented chicken manure, steel slag, and magnesium oxide used as raw materials was 0% for marine fertilizer Xd, 5% for marine fertilizer Xe, 11% for marine fertilizer Xf, 15% for marine fertilizer Xg, 20% for marine fertilizer Xh, 27% for marine fertilizer Xi, and 38% for marine fertilizer Xj. The results are shown in Figure 2.

図2からも分かるように、12重量部の発酵鶏糞と、4重量部の鉄鋼スラグと、酸化マグネシウムと、水分含量が45~60重量%となる量の水とを含む海域施肥材は、酸化マグネシウムの割合を1~4重量部の範囲内で変化させた場合にN/P=10~30の溶出を実現でき、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出が可能であることが示された。 As can be seen from Figure 2, a marine fertilizer containing 12 parts by weight of fermented chicken manure, 4 parts by weight of steel slag, magnesium oxide, and water in an amount that results in a moisture content of 45 to 60% by weight can achieve an N/P ratio of 10 to 30 when the proportion of magnesium oxide is changed within the range of 1 to 4 parts by weight, demonstrating the ability to dissolve nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks.

〔10.大型水槽での溶出成分確認試験〕
プレス機で作成した海域施肥材Xを100L水槽に入れ、海水かけ流しつつその溶出成分の濃度確認を行った。実験は半年間に亘って行われ、凡そ2週間毎に溶出成分の濃度の確認を行った。
[10. Testing to confirm eluted components in a large water tank]
The marine fertilizer material X made with the press was placed in a 100L tank, and the concentration of the eluted components was checked while seawater was poured over it. The experiment was carried out over a period of six months, and the concentration of the eluted components was checked approximately every two weeks.

その結果、期間中の平均N/Pモル溶出比は19.6であり、Fe/Pモル溶出比は0.06であった。すなわち、N/P=10~30でFe/P=0.001~0.1の溶出を実現でき、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出が可能であることが示された。 As a result, the average N/P molar elution ratio during the period was 19.6, and the Fe/P molar elution ratio was 0.06. In other words, it was possible to achieve elution of Fe/P = 0.001-0.1 at N/P = 10-30, demonstrating that it is possible to elution of nutrients suitable for the growth of algae, which serves as food for herbivorous bivalve mollusks.

〔11.フィールド試験〕
本実施形態に係る海域施肥材を尾道市浦崎の干潟に配置して、アサリの増殖を確認するフィールド試験を行った。3m×10mの区画を2つ設け、一方を試験区、他方を対照区に設定した。
11. Field Testing
The marine fertilizer according to this embodiment was placed on the tidal flats of Urasaki, Onomichi City, and a field test was conducted to confirm the proliferation of the clam. Two plots measuring 3m x 10m were set up, one as a test area and the other as a control area.

試験区には、本実施形態に係る海域施肥材Xを10個設置した。各海域施肥材Xは、同海域施肥材Xの高さと同程度の穴、例えば10~30cm程度の穴を干潟に形成して設置する工程と、同工程で形成した穴に海域施肥材Xを配置したのち、海域施肥材Xの上面を砂面とほぼ同等となるように埋没させると共に、この海域施肥材Xの上部をわずかの砂で被覆する工程とを経て設置した。 Ten marine fertilization materials X according to this embodiment were installed in the test area. Each marine fertilization material X was installed through a process of forming a hole in the tidal flat with a height equivalent to that of the marine fertilization material X, for example, a hole of about 10 to 30 cm, and placing the marine fertilization material X in the hole formed in the process, and then burying the marine fertilization material X so that its top surface was almost even with the sand surface, and covering the top of this marine fertilization material X with a small amount of sand.

また、試験区と対照区との両方に、平均殻長約26 mmのアサリをそれぞれ271個体/m2散布した。アサリ平均個体重量の経時変化を図3に示す。 In addition, 271 individual clams with an average shell length of approximately 26 mm were scattered in both the test and control areas. Figure 3 shows the change in average individual clam weight over time.

対照区に散布されたアサリ(3.68±0.60g)は、2ヶ月後には5.18±0.91g、4ヶ月後には5.93±1.15g、5ヶ月後には6.31±1.21g、6ヶ月後(試験終了時)には6.73±1.44gと変化した。また試験終了時のアサリの生存率は、散布時に対し78%であった。 The weight of the clams (3.68±0.60g) sprayed in the control area changed to 5.18±0.91g after two months, 5.93±1.15g after four months, 6.31±1.21g after five months, and 6.73±1.44g after six months (at the end of the experiment). The survival rate of the clams at the end of the experiment was 78% of that at the time of spraying.

一方、試験区に散布されたアサリ(対照区と同重量)は、2ヶ月後には5.30±0.90g、4ヶ月後には6.63±1.14g、5ヶ月後には6.95±1.56g、6ヶ月後(試験終了時)には6.88±1.50gと変化し、散布以降、対照区のアサリに比して良好な肥育傾向が見られた。特に、4ヶ月目以降は、対照区のアサリに対し有意な個体重量差が認められた(t-検定、p<0.05)。また試験終了時のアサリの生存率は、散布時に対し93%と対照区に比して高率であった。 On the other hand, the weight of the clams scattered in the test area (same weight as in the control area) changed to 5.30±0.90g after two months, 6.63±1.14g after four months, 6.95±1.56g after five months, and 6.88±1.50g after six months (at the end of the test), showing a tendency for better fattening compared to the clams in the control area after spraying. In particular, from the fourth month onwards, a significant difference in individual weight was observed compared to the clams in the control area (t-test, p<0.05). Furthermore, the survival rate of the clams at the end of the test was 93% compared to the time of spraying, which was higher than the control area.

また、対照区と試験区との双方の底泥中における栄養塩の濃度は、試験区では、溶存態無機窒素(DIN)、溶存態無機リン(DIP)、溶存態ケイ素(DSi)において有意に高い傾向が伺えた。ただし、溶出のタイミングとしては、DIN, DSiなどが早く、DIPが少し遅れる傾向が見られた。 In addition, the concentrations of nutrients in the bottom mud in both the control and test areas showed a tendency for dissolved inorganic nitrogen (DIN), dissolved inorganic phosphorus (DIP), and dissolved silicon (DSi) to be significantly higher in the test area. However, in terms of the timing of elution, DIN, DSi, etc. tended to be early, while DIP tended to be slightly delayed.

これらのことから、本実施形態に係る海域施肥材は、5ヶ月に亘る持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現でき、二枚貝の成長と生残を効果的に上げることができる施肥材であることが示された。 From these findings, it was shown that the marine fertilizer according to this embodiment is an organic fertilizer that has excellent durability over a period of five months, is made primarily from chicken manure, and is capable of dissolving nutrients suitable for the growth of algae that serves as food for herbivorous bivalve mollusks, making it a fertilizer that can effectively increase the growth and survival of bivalve mollusks.

上述してきたように、本実施形態に係る海域施肥材によれば、12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水とを含む柱状圧縮成形体よりなることとしたため、持続性に優れた有機肥料であって鶏糞由来のものを主要な構成材料としつつ、植食性二枚貝の餌となる藻類の生育に適した栄養成分の溶出を実現でき、二枚貝の成長と生残を効果的に上げることができる施肥材である。 As described above, the marine fertilizer according to this embodiment is made of a columnar compressed molded body containing 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water that makes the moisture content of the marine fertilizer described below 45 to 60% by weight. This makes it a highly sustainable organic fertilizer that is mainly made of chicken manure and can dissolve nutrients suitable for the growth of algae that serve as food for herbivorous bivalve mollusks, making it a fertilizer that can effectively increase the growth and survival of bivalve mollusks.

最後に、上述した各実施の形態の説明は本発明の一例であり、本発明は上述の実施の形態に限定されることはない。このため、上述した各実施の形態以外であっても、本発明に係る技術的思想を逸脱しない範囲であれば、設計等に応じて種々の変更が可能であることは勿論である。 Finally, the above-mentioned explanations of each embodiment are merely examples of the present invention, and the present invention is not limited to the above-mentioned embodiments. Therefore, even if the embodiment is different from the above-mentioned embodiments, various modifications can be made depending on the design, etc., as long as they do not deviate from the technical concept of the present invention.

Claims (6)

12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水とを含む混合材料(ただし、同混合材料の全体を固化できる量のセメントが含まれたものを除く。)の圧縮成形体よりなり、海水にN/P=10~30、Fe/P=0.001~0.1の割合で溶出可能に構成した海域施肥材。 A marine fertilizer material that is made of a compressed molded body of a mixed material (excluding those that contain an amount of cement that is sufficient to solidify the entire mixed material) containing 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water that makes the moisture content of the marine fertilizer material described below 45 to 60% by weight , and is configured to be soluble in seawater at a ratio of N/P = 10 to 30 and Fe/P = 0.001 to 0.1. 12重量部の発酵鶏糞と、2~6重量部の粒状鉄と、1~4重量部の酸化マグネシウムと、後記海域施肥材の水分含量が45~60重量%となる量の水との混合材料(ただし、同混合材料の全体を固化できる量のセメントが含まれたものを除く。)を圧縮成形し海水にN/P=10~30、Fe/P=0.001~0.1の割合で溶出可能とすることを特徴とする海域施肥材の製造方法。 A method for producing a marine fertilizer material, comprising compressing and molding a mixture of 12 parts by weight of fermented chicken manure, 2 to 6 parts by weight of granular iron, 1 to 4 parts by weight of magnesium oxide, and an amount of water such that the moisture content of the marine fertilizer material described below is 45 to 60% by weight (excluding mixtures containing an amount of cement sufficient to solidify the entire mixture), and making the mixture soluble in seawater at a ratio of N/P = 10 to 30 and Fe/P = 0.001 to 0.1. 前記混合材料は、前記溶出のバランスが保たれる範囲内で腐葉土及び/または培養土を補助原料として含むことを特徴とする請求項2に記載の海域施肥材の製造方法 The method for manufacturing a marine fertilizer material according to claim 2, characterized in that the mixed material contains leaf mold and/or culture soil as auxiliary raw materials within a range in which the balance of the elution is maintained. 前記発酵鶏糞は、
鶏糞と同鶏糞よりも水分含量が低い水分調整材との混合物に対し鶏糞発酵微生物発酵液を添加して水分含量を60±5%に調整した被発酵混合物を調製する工程と、
得られた被発酵混合物を堆積させて発酵を助長する工程と、
被発酵混合物の温度が70℃以上となった際に、80℃に達する前に切り返しを行い、再び被発酵混合物を堆積させる切り返し工程と、
水分含量が35%以下となり、且つ、温度が45℃以上に昇温しなくなるまで前記切り返し工程を繰り返す繰返工程と、
繰返工程を経た被発酵混合物を、必要に応じ更なる追加発酵工程に供した上で発酵鶏糞とする発酵鶏糞生成工程と、
を経て製造したものであることを特徴とする請求項2に記載の海域施肥材の製造方法。
The fermented chicken manure is
A step of preparing a fermented mixture by adding a fermentation liquid of a chicken manure fermenting microorganism to a mixture of chicken manure and a moisture adjusting material having a lower moisture content than the chicken manure to adjust the moisture content to 60±5%;
piling the resulting fermented mixture to facilitate fermentation;
A turning step in which, when the temperature of the fermented mixture reaches 70°C or higher, the mixture is turned over before it reaches 80°C and the fermented mixture is piled up again;
a repeating step of repeating the turning step until the moisture content becomes 35% or less and the temperature does not rise to 45° C. or more;
A fermented chicken manure production process in which the fermented mixture that has been subjected to the repeating process is subjected to a further additional fermentation process as necessary to produce fermented chicken manure;
The method for producing a marine fertilizer material according to claim 2, characterized in that the material is produced through the steps of:
前記鶏糞発酵微生物発酵液は、
0.6重量部の乾燥ステビア茎粉末と、0.6重量部の米ぬか粉末と、0.6重量部の乾燥おから粉末と、耐塩性酵母を少なくとも含有する11~13重量部の汽水と、を混合した混合液を所定時間静置する静置工程と、
前記静置工程を経た混合液を所定の容器に収容し、収容された混合液に同混合液の収容形状の外表面上のいずれの位置からも10cm以上であり、且つ、外表面上の少なくともいずれかの位置から17cm以下となる弱殺菌領域を形成する容器収容工程と、
前記容器収容工程を経て混合液を収容した所定の容器を加熱空間内に配置し、同加熱空間を常温常圧の状態から約2.5気圧で150~160℃の状態にまで45~60分掛けて昇温し、約2.5気圧で150~160℃の状態を1~3分間維持し、その後加熱空間を約2気圧で115~125℃の状態にまで3~5分間掛けて降温設定し、約2気圧で115~125℃の状態を20~40分間維持し、更に加熱空間を常温常圧の状態にまで24~30時間掛けて降温させて、前記混合液中に加熱選抜された微生物を残存させる微生物選抜工程と、
少なくとも微生物が液相に移行可能な手段により前記微生物選抜工程を経た混合液を固液分離して微生物含有液を得る固液分離工程と、
得られた微生物含有液に糖源を添加して常温常圧で所定時間発酵し、微生物含有液のpHを4.5以下で、且つ、酸化還元電位を-100mV以下とする第1の発酵工程と、
第1の発酵工程を経た微生物含有液にステビア茎の熟成液を添加してpHが3.1以下となるまで発酵させて不良発酵防止剤とする第2の発酵工程と、を経て得られた発酵液であることを特徴とする請求項4に記載の海域施肥材の製造方法
The chicken manure fermentation microorganism fermentation liquid is
A step of allowing a mixture of 0.6 parts by weight of dried stevia stem powder, 0.6 parts by weight of rice bran powder, 0.6 parts by weight of dried soybean pulp powder, and 11 to 13 parts by weight of brackish water containing at least a salt-tolerant yeast to stand for a predetermined period of time;
A container containing step of containing the mixed liquid having been subjected to the standing step in a predetermined container and forming a weak sterilization region in the contained mixed liquid that is 10 cm or more from any position on the outer surface of the container shape of the mixed liquid and 17 cm or less from at least any position on the outer surface;
a microorganism selection process in which the predetermined container containing the mixed liquid after the container placement process is placed in a heating space, the heating space is heated from room temperature and normal pressure to 150-160°C at about 2.5 atmospheres over a period of 45-60 minutes, the state of 150-160°C at about 2.5 atmospheres is maintained for 1-3 minutes, the heating space is then cooled to 115-125°C at about 2 atmospheres over a period of 3-5 minutes, the state of 115-125°C at about 2 atmospheres is maintained for 20-40 minutes, and the heating space is further cooled to room temperature and normal pressure over a period of 24-30 hours, thereby allowing the microorganisms selected by heating to remain in the mixed liquid;
a solid-liquid separation step of obtaining a microorganism-containing liquid by subjecting the mixed liquid having been subjected to the microorganism selection step to solid-liquid separation using a means capable of transferring at least the microorganism to a liquid phase;
a first fermentation step in which a sugar source is added to the obtained microorganism-containing liquid and fermented at room temperature and normal pressure for a predetermined time to adjust the pH of the microorganism-containing liquid to 4.5 or less and the redox potential to -100 mV or less;
The method for producing a marine fertilizer according to claim 4, characterized in that the fermented liquid is obtained by adding a matured liquid of stevia stem to the microorganism-containing liquid that has been subjected to the first fermentation step, and fermenting the liquid until the pH becomes 3.1 or less to obtain a defective fermentation inhibitor.
請求項1に記載の海域施肥材又は請求項2~5のいずれか1項に記載の海域施肥材の製造方法にて製造された海域施肥材の設置方法であって、
海域施肥材の高さと同程度の穴を干潟に形成して設置する工程と、
形成した穴に海域施肥材を配置したのち、同海域施肥材の上部をわずかの砂で被覆する工程と、
を有することを特徴とする海域施肥材の設置方法。
A method for installing a sea area fertilizer material manufactured by the method for manufacturing a sea area fertilizer material according to claim 1 or any one of claims 2 to 5 ,
A step of forming and installing a hole in the tidal flats at a height equivalent to that of the marine fertilizer material;
A step of placing a sea area fertilizer in the formed hole and then covering the top of the sea area fertilizer with a small amount of sand;
A method for installing a marine fertilization material, comprising the steps of:
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000143375A (en) 1998-11-05 2000-05-23 Taki Chem Co Ltd Compost
JP2002121553A (en) 2000-11-15 2002-04-26 Bakuto Material:Kk Organic soil conditioner for slope works and planting works
JP2013017462A (en) 2011-07-14 2013-01-31 Nippon Steel & Sumikin Engineering Co Ltd Method for forming fish reef block and seaweed bed
JP2017099339A (en) 2015-12-02 2017-06-08 トリゼンフーズ株式会社 Screening method of microorganisms for poor fermentation preventing agents and production method of poor fermentation preventing agent as well as fermentation method of biomass using poor fermentation preventing agent obtained by the same method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000143375A (en) 1998-11-05 2000-05-23 Taki Chem Co Ltd Compost
JP2002121553A (en) 2000-11-15 2002-04-26 Bakuto Material:Kk Organic soil conditioner for slope works and planting works
JP2013017462A (en) 2011-07-14 2013-01-31 Nippon Steel & Sumikin Engineering Co Ltd Method for forming fish reef block and seaweed bed
JP2017099339A (en) 2015-12-02 2017-06-08 トリゼンフーズ株式会社 Screening method of microorganisms for poor fermentation preventing agents and production method of poor fermentation preventing agent as well as fermentation method of biomass using poor fermentation preventing agent obtained by the same method

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