JP2007039253A - Organic silicate fertilizer - Google Patents
Organic silicate fertilizer Download PDFInfo
- Publication number
- JP2007039253A JP2007039253A JP2005221794A JP2005221794A JP2007039253A JP 2007039253 A JP2007039253 A JP 2007039253A JP 2005221794 A JP2005221794 A JP 2005221794A JP 2005221794 A JP2005221794 A JP 2005221794A JP 2007039253 A JP2007039253 A JP 2007039253A
- Authority
- JP
- Japan
- Prior art keywords
- fertilizer
- fly ash
- urine
- livestock
- organic
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Landscapes
- Processing Of Solid Wastes (AREA)
- Fertilizers (AREA)
Abstract
Description
本発明は、有機ケイ酸肥料の製造方法、または該肥料を混合した肥料に関し、詳しくは、産業廃棄物の一つであるフライアッシュに家畜からの尿液を吸着させて有機ケイ酸肥料を製造する方法、及びカリウム化合物等を加えてカリウムに富んだ有機ケイ酸肥料、及び該肥料を含有する水稲用肥料に関する。 The present invention relates to a method for producing an organic silicate fertilizer, or a fertilizer mixed with the fertilizer, and more specifically, an organic silicate fertilizer is produced by adsorbing urine from livestock to fly ash, which is one of industrial wastes. And an organic silicate fertilizer rich in potassium by adding a potassium compound and the like, and a fertilizer for paddy rice containing the fertilizer.
電気を安定して供給するため、石炭は他の化石燃料に比べ、供給の安定性や経済性に優れており石油代替エネルギーとして原子力に次ぐものとして位置づけられており、石炭火力発電設備は、平成14年度末で3,377万KWあり、平成19年度3,922万KW、平成24年度4,315万KWになるように計画されているといわれている。このように石炭火力発電設備が増加すると、発生するフライアッシュ(石炭灰)も増加し、全国のフライアッシュ(石炭灰)の発生量は平成14年度末の約920万トンが、平成19年度末には約1,000万トンに達するものと予測される。このように大量に発生するフライアッシュ(石炭灰)を資源として有効活用するため、研究開発が積極的に行われている。
フライアッシュの有効利用としては、その化学的・物理的性質を活かして多くの分野で使用されており、セメント混合剤、道路材、建材、農水産の分野等に利用されている。
In order to supply electricity stably, coal is superior to other fossil fuels in terms of supply stability and economy, and is positioned as the next alternative to nuclear power as an alternative energy to oil. It is said that there are 33.77 million KW at the end of 2014, planned to be 39.22 million KW in 2007 and 43.15 million KW in 2012. As coal-fired power generation facilities increase in this way, the amount of fly ash (coal ash) generated also increases, and the amount of fly ash (coal ash) generated nationwide is about 9.2 million tons at the end of 2002, the end of 2007 Is estimated to reach about 10 million tons. In order to effectively utilize such a large amount of fly ash (coal ash) generated as a resource, research and development are actively carried out.
As an effective use of fly ash, it is used in many fields taking advantage of its chemical and physical properties, and is used in the fields of cement admixtures, road materials, building materials, agriculture and fisheries.
フライアッシュは、その成分がケイ酸を主体とするものであり、その他、古代植物が自らの成長のため取り込んだホウ素、石灰、鉄など作物に有用な多くの微量要素も含んでいる。しかしながら、このままでは作物に吸収されず、フライアッシュ単独で、肥料として用いることはできない。 Fly ash is composed mainly of silicic acid, and it also contains many trace elements useful for crops such as boron, lime, and iron that ancient plants have taken up for their growth. However, as it is, it is not absorbed by the crops, and fly ash alone cannot be used as a fertilizer.
従来、フライアッシュを一原料として肥料に用いる技術として、生活廃棄物や畜産廃棄物等の有機物を微生物により発酵させるようにした有機物の堆肥化方法において、前記有機物内へのケイ酸塩鉱物とフライアッシュ等との混合物を混合することにより、有機物の発酵を促進させる有機物の堆肥化方法(例えば、特許文献1参照)や、有機汚泥より肥料を製造する方法において、(1)脱水前の有機汚泥に対して、フライアッシュを有機汚泥の固形分当たり50〜200重量%加え、撹拌・混合する工程、(2)次いで高分子凝集材を該混合汚泥の固形分当たり0.3〜2.0重量%加え撹拌し、含水率60〜75重量%に脱水する工程、(3)次いで前工程で得られた脱水汚泥に対して発酵助材としてムギワラ、イネワラ、おがくず、バーク(樹皮)等を添加後の汚泥の含水率が55〜73重量%になるように加えて混合した後発酵させる工程、からなる有機汚泥より肥料を製造する方法(例えば、特許文献2)や、木質を含む有機質の炭素源に水および窒素源を混合し、この混合物を大気中で発酵させて腐食化する堆肥の製造方法において、前記混合物に対し、さらにフライアッシュ等の石炭灰を添加混合する木質原料堆肥の製造方法(例えば、特許文献3参照)が知られている。 Conventionally, as a technique for using fly ash as a raw material for fertilizers, in a method for composting organic matter in which organic matter such as domestic waste and livestock waste is fermented by microorganisms, silicate minerals and fly in the organic matter are used. In a method for composting organic matter that promotes fermentation of organic matter by mixing a mixture with ash or the like (see, for example, Patent Document 1) and a method for producing fertilizer from organic sludge, (1) Organic sludge before dehydration In contrast, the step of adding fly ash in an amount of 50 to 200% by weight per solid content of organic sludge, stirring and mixing, (2) and then the polymer agglomerate in the amount of 0.3 to 2.0 weight per solid content of the mixed sludge (3) Subsequently, wheat straw, rice straw, sawdust, baked rice bran as fermentation aids for the dehydrated sludge obtained in the previous step. A method for producing fertilizer from organic sludge comprising, for example, a step of adding and mixing so that the moisture content of sludge after addition of ku (bark) is 55 to 73% by weight, followed by fermentation (for example, Patent Document 2) In the method of manufacturing compost, which mixes water and nitrogen sources with organic carbon sources including wood, and ferments the mixture in the atmosphere to corrode, the mixture is further mixed with coal ash such as fly ash There is known a method for producing woody raw material compost (see, for example, Patent Document 3).
また、家畜糞肥料の製造方法において、家畜糞をパルプ、フライアッシュ等の水分吸収材料の存在下で細分割化する家畜糞肥料の製造方法(例えば、特許文献4参照)や、堆積発酵し得る有機物と石炭ボイラーから副製品として産出するクリンカーアッシュ並びにフライアッシュを30〜70:70〜0:0〜70の容積比で混合し発酵させた土壌改良効果を有する有機肥料(例えば、特許文献5参照)が知られている。 In addition, in the method for producing livestock manure, a method for producing livestock manure that subdivides livestock feces in the presence of a moisture-absorbing material such as pulp and fly ash (see, for example, Patent Document 4), and sediment fermentation. Organic fertilizer having a soil improvement effect obtained by mixing and fermenting clinker ash and fly ash produced as by-products from an organic substance and a coal boiler at a volume ratio of 30 to 70:70 to 0: 0 to 70 (see, for example, Patent Document 5) )It has been known.
一方、家畜の尿の処理技術としては、家畜の尿が貯蔵される尿貯蔵槽と、前記尿貯留槽から所定量の尿が投入され、少なくとも1種類以上のバクテリア混入の所定量の水が入れられた所定大の曝気槽と、前記曝気槽内の底部に設けられ、エアポンプから送られた外気により、前記曝気槽にエアーレーションを行う曝気器と、前記曝気槽からの家畜尿を含む水の一部が投入される脱窒槽と、前記脱窒槽から投入された家畜尿を含む水の一部を、大気中の酸素と反応させて硝酸塩を生成して前記脱窒槽に再投入する硝化槽と、前記硝化槽の家畜尿を含む水の一部を濾過する濾過装置と、前記硝化槽により濾過され、前記曝気槽に再投入される水が貯水される処理済貯水槽と、からなる水循環式汚物処理装置(例えば、特許文献6参照)が知られている。 On the other hand, livestock urine treatment technology includes a urine storage tank for storing livestock urine, a predetermined amount of urine from the urine storage tank, and a predetermined amount of water mixed with at least one kind of bacteria. An aeration tank of a predetermined size, an aerator provided at the bottom of the aeration tank, and aerating the aeration tank by outside air sent from an air pump; and water containing livestock urine from the aeration tank A denitrification tank into which a part is charged, and a nitrification tank in which a part of water containing livestock urine charged from the denitrification tank is reacted with oxygen in the atmosphere to generate nitrate and re-enter the denitrification tank. A water circulation system comprising: a filtration device for filtering part of water containing livestock urine in the nitrification tank; and a treated water tank for storing water that is filtered by the nitrification tank and re-entered into the aeration tank A waste disposal apparatus (see, for example, Patent Document 6) is known. That.
本発明の課題は、廃棄物を有効利用して肥料を製造することを目的とするものであり、特に産業廃棄物であるフライアッシュや畜産公害として問題の大きい畜尿を利用して、無機のフライアッシュを有機の型に変え、肥料原料やこれを含む肥料、及び水稲用肥料、それらの製造方法を提供することにある。特に稲は好んでケイ酸を吸収する植物であり、ケイ酸分を供給する土づくりは、高品質・高収量を目指す基本となっており、玄米100kgの稲は20kgのケイ酸分を吸収するといわれ、反収600kgの米を収穫するには、120kgのケイ酸が毎年必要とされることになる。また、稲の生育にはケイ酸と共にカリウムも重要な元素であり、籾殻の養分が米粒に移行するのに、カリウムが関与するといわれている。稲の登熟が終わるまで、カリウム分の集積の高いものでは、稔実籾となり、登熟後期にカリウム分の保持が低下しているものでは、不稔籾になりやすい。したがって、カリウムは窒素やリン酸と違って、かなり生育の後期まで供給しなければならない。カリウムの効果は作物体内の膨圧も維持するので、旱ばつへの抵抗性を強め、炭水化物の合成にも関与し、全体としての籾のサイズを大きくするので、二次枝梗の籾の発達も高め、増収・品質向上に寄与している。さらに、カリウムは水稲の栽培全期を通じて休みなく、適切な量を連続的に吸収させる重要な成分でもあり、本発明は、ケイ酸、カリウムを含有する特に水稲に適した、効率的な肥料を提供する。 An object of the present invention is to produce fertilizer by effectively using waste, and in particular, using fly ash that is industrial waste and livestock urine which is a big problem as livestock pollution, An object of the present invention is to provide a fertilizer raw material, a fertilizer containing the fertilizer, a fertilizer for paddy rice, and a production method thereof by changing fly ash into an organic mold. In particular, rice is a plant that prefers to absorb silicic acid, and the creation of soil that supplies silicic acid is the basis for high quality and high yield, and 100 kg of brown rice absorbs 20 kg of silicic acid. It is said that 120 kg of silicic acid is required every year to harvest 600 kg of rice. Potassium is also an important element for the growth of rice, and it is said that potassium is involved in the transfer of rice husk nutrients to rice grains. Until rice ripening is completed, those with a high accumulation of potassium become cocoon seeds, and those with a reduced potassium retention in the later stage of ripening tend to be sterile. Therefore, unlike nitrogen and phosphoric acid, potassium must be supplied until a very late stage of growth. The effect of potassium also maintains the turgor pressure in the crop body, which increases resistance to drought, contributes to carbohydrate synthesis, and increases the overall size of the cocoon, so that the development of pods in secondary branching It also contributes to increased sales and quality. Furthermore, potassium is an important component that absorbs an appropriate amount continuously throughout the entire cultivation period of paddy rice, and the present invention provides an efficient fertilizer particularly suitable for paddy rice containing silicic acid and potassium. provide.
従来、フライアッシュと家畜糞尿、その他木屑等の繊維質成分と混合して発酵させ、肥料とすることは広く知られていたが、フライアッシュの主成分であるケイ酸を無機から有機の型に変え、最大限に活用するための肥料原料として、およびカリ肥料を配合してケイ酸質およびカリウムに富んだ肥料を得るため、本発明者らはフライアッシュと種々の他の廃棄処理されている材料との組合せについて鋭意研究した結果、家畜尿との組み合わせが肥料原料として有効であることを見い出し、本発明を完成するに至った。 Conventionally, it has been widely known that fly ash is mixed with fiber components such as livestock manure and other wood chips and fermented to make fertilizer, but the main component of fly ash is changed from inorganic to organic type. As a fertilizer raw material to change and make the best use of, and to combine the potash fertilizer to obtain fertilizer rich in siliceous and potassium, we have made fly ash and various other waste materials As a result of earnest research on the combination with urine, it was found that the combination with livestock urine was effective as a fertilizer raw material, and the present invention was completed.
すなわち本発明は、(1)フライアッシュに家畜尿を吸着させ、発酵させることを特徴とする有機ケイ酸肥料の製造方法や、(2)フライアッシュを、強度が高く液体の浸透性がよい素材からなる袋に収容し、そのフライアッシュ入り袋を家畜尿溜り池に漬けこんで尿液を飽和するまで吸着させ、堆肥の発酵槽に搬入して発酵することを特徴とする前記(1)記載の有機ケイ酸肥料の製造方法に関する。 That is, the present invention includes (1) a method for producing an organic silicate fertilizer characterized by adsorbing and fermenting livestock urine to fly ash, and (2) a material having high strength and good liquid permeability. (1), wherein the fly ash bag is soaked in a livestock urine pond, adsorbed until the urine is saturated, carried into a compost fermenter and fermented. The present invention relates to a method for producing an organic silicate fertilizer.
また本発明は、(3)フライアッシュに家畜尿を吸着、発酵させてなる有機ケイ酸肥料や、(4)フライアッシュに家畜尿を吸着・発酵させた有機ケイ酸含有肥料原料とカリウム含有化合物とを含むことを特徴とする肥料や、(5)フライアッシュに家畜尿を吸着・発酵させた有機ケイ酸含有肥料原料とカリウム含有化合物とマグネシウム含有化合物を含むことを特徴とする肥料や、(6)前記(3)〜(5)のいずれか記載の肥料を水稲用肥料として用いることを特徴とする水稲用肥料に関する。 The present invention also includes (3) an organic silicate fertilizer obtained by adsorbing and fermenting livestock urine to fly ash, and (4) an organic silicate-containing fertilizer material and potassium-containing compound obtained by adsorbing and fermenting livestock urine to fly ash. And (5) a fertilizer characterized by containing an organic silicate-containing fertilizer raw material obtained by adsorbing and fermenting livestock urine to fly ash, a potassium-containing compound, and a magnesium-containing compound ( 6) A fertilizer for paddy rice, wherein the fertilizer according to any one of (3) to (5) is used as a fertilizer for paddy rice.
本発明の有機ケイ酸肥料原料およびそれを含む肥料は、産業廃棄物のフライアッシュや畜産公害として問題となっている畜尿を利用して、廃棄物の処理に貢献するばかりでなく、有機ケイ酸肥料として質の高い、そしてカリ肥料及び/又はマグネシウム肥料と混用して、「カリウム」が苦溶性のカリ肥料に変わり、ケイ酸が作物によく吸収される有機ケイ酸肥料とすることができる。 The organic silicate fertilizer raw material of the present invention and the fertilizer containing the raw material not only contribute to the treatment of waste by using fly ash of industrial waste and livestock urine that is a problem of animal husbandry pollution, but also organic silica. It can be mixed with potassium fertilizer and / or magnesium fertilizer of high quality as acid fertilizer, and “potassium” can be changed to bitter-soluble potassium fertilizer, and organic silicic acid fertilizer in which silicic acid is well absorbed by crops can be obtained.
本発明の有機ケイ酸肥料の製造方法としては、フライアッシュに家畜尿を吸着させ、発酵させる方法であれば特に限定されるものではなく、ここでの家畜尿とは、家畜糞と家畜尿とを固液分離した尿液を意味する。フライアッシュとしては、通常の石炭火力発電所から発生する、フライアッシュとして排出されたものを用いることができ、家畜尿は、牛、豚が主であるが、その他、馬、羊等から排出されたものを用いることができる。 The method for producing the organic silicate fertilizer of the present invention is not particularly limited as long as it is a method of adsorbing and fermenting livestock urine to fly ash, and livestock urine here refers to livestock feces and livestock urine. Means urine fluid separated into solid and liquid. As fly ash, the one generated from ordinary coal-fired power plants and discharged as fly ash can be used. Livestock urine is mainly cows and pigs, but is also discharged from horses, sheep, etc. Can be used.
フライアッシュに家畜尿を吸着させる方法としては、フライアッシュを単に家畜尿と混ぜるのでは、フライアッシュが飛散して効率が悪く、そのため、強度が高く液体浸透しやすい例えばナイロン製、ビニール製等を素材とする袋にフライアッシュを収容し、その後、フライアッシュ収容の袋を尿溜り(池)に入れて家畜尿をフライアッシュに吸着させて製造する方法が好ましい。 As a method of adsorbing livestock urine to fly ash, fly ash is simply mixed with livestock urine, so fly ash is scattered and inefficient, so it is strong and easy to penetrate liquid, such as nylon, vinyl etc. A method is preferred in which fly ash is accommodated in a bag as a raw material, and then the fly ash-accommodated bag is placed in a urine pool (pond) and the livestock urine is adsorbed to the fly ash.
発酵は、従来の堆肥の醗酵を行う発酵槽で実施することができ、家畜の尿液に含まれるN、P、Kを培養基質とし、特にアンモニアから転換する窒素の含有率が高いものである。堆積する堆肥の発酵と同様に、通常、自然醗酵により、発酵し醗酵熱が発生する。発酵熱は、大気中や有機質炭素源などに付着している好気性微生物によって原料の有機物が分解される過程で発生する。このような発酵熱を利用して管理される好ましい発酵槽の温度条件は、60〜80℃程度である。なぜなら、60℃未満の低温では醗酵反応が遅くなり、80℃を越えるように加熱すると、微生物の成育が悪くなって醗酵が進まなくなるからである。
上記発酵の際、家畜等糞、木屑等適宜添加することができる。
Fermentation can be carried out in a conventional fermenter for fermenting compost, and N, P, K contained in the urine of livestock is used as a culture substrate, and in particular, the content of nitrogen that is converted from ammonia is high. . Like fermentation of the compost which accumulates, it ferments and a fermentative heat generate | occur | produces normally by natural fermentation. Fermentation heat is generated in the process of decomposing organic materials as raw materials by aerobic microorganisms attached to the atmosphere or organic carbon sources. The temperature condition of the preferable fermenter managed using such fermentation heat is about 60-80 degreeC. This is because the fermentation reaction is slow at a low temperature of less than 60 ° C., and if it is heated to exceed 80 ° C., the growth of microorganisms deteriorates and the fermentation does not proceed.
During the fermentation, feces such as livestock and wood chips can be added as appropriate.
具体的には、まず、家畜尿吸着フライアッシュを袋より取り出して、堆肥の発酵槽(通常堆肥などを発酵して肥料を製造するタンクを指す)において、家畜尿吸着フライアッシュと2次発酵槽よりの戻し堆肥とよく混合し、混合したものを1次発酵槽において吸引・送気しながら10日間前後発酵し、次に2次発酵槽に移して吸引・送気しながら7日間前後発酵し、ここでの発酵物の約90%は湿潤混合槽に戻す。2次発酵槽からの発酵物を3次発酵槽に移し50日間前後送気しながら発酵する。その後害発酵物を90日前後生成物置場にて、送気しながら乾燥して、水分約20%の発酵物が得られる。
上記湿潤
Specifically, first, the livestock urine adsorption fly ash is taken out from the bag, and in the compost fermenter (usually a tank that ferments fertilizer etc. to produce fertilizer), the livestock urine adsorbent fly ash and the secondary fermenter Mix well with the back compost and ferment the mixture for about 10 days while sucking and feeding it in the primary fermenter, then transfer it to the secondary fermenter and ferment for about 7 days while sucking and feeding it. About 90% of the fermented product here is returned to the wet mixing tank. The fermented material from the secondary fermenter is transferred to the tertiary fermenter and fermented while being fed for about 50 days. Thereafter, the fermented fermented product is dried for about 90 days while being fed in the product place, and a fermented product having a water content of about 20% is obtained.
Above wetting
フライアッシュは、前記のとおりのものを用いるが、JIS規格によれば、シリカ45%以上、水分1%以下、強熱減量8%以下、比重1.95以上、比表面積1500cm 2 /g以上のものであるが、このような規格化されたフライアッシュ を使用することができることは勿論である。 The fly ash is as described above. According to JIS standards, silica 45% or more, moisture 1% or less, ignition loss 8% or less, specific gravity 1.95 or more, specific surface area 1500 cm 2 / g or more. Of course, such a standardized fly ash can be used.
本発明の他の肥料としては、フライアッシュに家畜尿を吸着・発酵させた有機ケイ酸肥料(以下、「フライアッシュ発酵物」という場合がある)とカリウム含有化合物とを含むものであれば、特に制限されるものではない。一般に、カリ肥料として、即効性の塩化カリウムと硫酸カリウムが主流であるが、本発明では、ゆっくり効いて、濃度障害がない新しい緩効性カリ肥料とすることができる。 As the other fertilizer of the present invention, if it contains an organic silicate fertilizer obtained by adsorbing and fermenting livestock urine to fly ash (hereinafter sometimes referred to as “fly ash fermented product”) and a potassium-containing compound, There is no particular limitation. In general, quick-acting potassium chloride and potassium sulfate are mainly used as potash fertilizer, but in the present invention, a slow-acting potash fertilizer that works slowly and does not have a concentration disturbance can be obtained.
本発明の他の肥料としては、フライアッシュに家畜尿を吸着・発酵させた有機ケイ酸肥料とカリウム含有化合物とマグネシウム含有化合物を含むものであれば、特に制限されるものではない。 The other fertilizer of the present invention is not particularly limited as long as it contains an organic silicate fertilizer obtained by adsorbing and fermenting livestock urine to fly ash, a potassium-containing compound, and a magnesium-containing compound.
従来の、フライアッシュとカリウム含有化合物と、その他苦土源の水酸化マグネシウムやドロマイトを混合、造粒し、比較的低温で焼成することで、カリウム含有化合物は、「苦溶性」のカリ肥料に変わり、「ケイ酸」は作物によく吸収されるが、本発明のフライアッシュ発酵物でも、このような効果を奏するものである。 By mixing and granulating conventional fly ash, potassium-containing compounds, and other magnesium sources such as magnesium hydroxide and dolomite, and calcining them at a relatively low temperature, the potassium-containing compounds turn into “bitter-soluble” potash fertilizers. However, “silicic acid” is well absorbed by crops, but the fly ash fermented product of the present invention has such an effect.
一般にケイ酸カリ肥料は、苦溶性のため水に溶けず、雨水や、かん水によって流れ出すことがなく、そして苦溶性となることにより、作物の根から出る根酸によって溶けるので、作物の必要量だけ吸収され、カリ肥料で問題となる過多吸収になるようなことは起こらない。本発明のフライアッシュ発酵物でも、上記のような作用・機作を行っていると思われる。 Generally, potassium silicate fertilizer does not dissolve in water because it is bitter-soluble, it does not flow out due to rainwater or brackish water, and by becoming bitter-soluble, it is dissolved by the root acid coming from the root of the crop, so it absorbs only the necessary amount of crop And there is no such thing as excessive absorption, which is a problem with potash fertilizer. The fly ash fermented product of the present invention is considered to perform the above-described action and mechanism.
本発明のフライアッシュ発酵物とカリウムを含有した肥料は、土を酸性化する成分を含んでいないので、施肥量を多くしても土壌の塩類濃度を高めず濃度障害を起こすようなことはなく、また、ケイ酸カリ肥料のカリ成分を必要とするときだけ、必要なだけ溶かし吸収するので、作物体中のカリ濃度を必要以上に高めないので、石灰、苦土がバランスよく吸収されることになり、生理障害を生じさせない。 Since the fertilizer containing the fly ash fermented product and potassium of the present invention does not contain a component that acidifies the soil, increasing the amount of fertilization does not increase the salt concentration of the soil and does not cause concentration disturbance. Also, only when the potash component of potassium silicate fertilizer is needed, it dissolves and absorbs as much as necessary, so the potash concentration in the crop body is not increased more than necessary, so that lime and bitter soil are absorbed in a balanced manner. It does not cause physiological disorder.
本発明のカリ入りフライアッシュ発酵物肥料は、従来のケイ酸カリ肥料と同様に、稲の受光体勢がよくなること、光合成が衰えないこと、冷害などの異常気象に強い稲を作ること、ケイ酸の利用率が高いことから病害虫に強いこと、生育後期に養分供給を促進すること、根張りがよくなり、根毛が多いこと、稲が倒れにくくなる効果を奏する。 As with conventional potassium silicate fertilizers, the fly ash fermented fertilizer with potash of the present invention has an improved rice photosensitivity, does not decay photosynthesis, makes rice resistant to abnormal weather such as cold damage, It is highly resistant to pests due to its high utilization rate, promotes nutrient supply at the later stage of growth, has good rooting, has many root hairs, and has the effect of making rice less likely to fall.
以下、実施例により本発明をより具体的に説明するが、本発明の技術的範囲はこれらの例示に限定されるものではない。 EXAMPLES Hereinafter, although an Example demonstrates this invention more concretely, the technical scope of this invention is not limited to these illustrations.
(家畜尿吸着フライアッシュの製法)
フライアッシュとしては、SiO2:52.3%、Al2O3:26.6%、CaO:9.4%、Fe2O3:5.6%、K2O:1.1%、B2O3:0.4%の配合割合のものを用いた。このフライアッシュ20kgをビニール製の袋に収容し、15個の袋、計300kgを牛の尿1000kLの入った尿溜り池に入れ、3日間放置し、フライアッシュに牛の尿を吸着させた。該フライアッシュ袋を堆肥の発酵槽に搬入した。
(Manufacturing method of livestock urine adsorption fly ash)
The fly ash, SiO 2: 52.3%, Al 2 O 3: 26.6%, CaO: 9.4%, Fe 2 O 3: 5.6%, K 2 O: 1.1%, B 2 O 3 : 0.4% blending ratio was used. 20 kg of this fly ash was accommodated in a plastic bag, and 15 bags, a total of 300 kg, were placed in a urine pond containing 1000 kL of cow urine and left for 3 days to adsorb the cow urine to the fly ash. The fly ash bag was carried into a compost fermenter.
(フライアッシュ発酵物の製法)
実施例1により得られた尿吸着フライアッシュを生フン置場兼浸潤混合槽に53t/日(水分83.0%)搬入し2次発酵槽において発酵した発酵物を戻し堆肥とよく混合し、水分62%となるまで調整し、1次発酵槽にて10日間、吸引・送気を繰り返し発酵させて水分42.0%となり、2次発酵槽にて7日間、吸引・送気を繰り返しながら発酵させて水分36.0%となった。その約90%を前記浸潤混合槽に戻し、残りの10%(水分35.0%)を3次発酵槽(50日間)に送気しながら発酵させた(水分25.0%)。さらに生成物置場にて88日間滞留送気しながら発酵熟成させた。水分20.0%の最終製品8.0t/日を得た。
(Production method of fermented fly ash)
The urine adsorption fly ash obtained in Example 1 was carried into a raw dung yard / infiltration mixing tank at 53 t / day (water content 83.0%), and the fermented material fermented in the secondary fermenter was returned and mixed well with compost. Adjust to 62% and repeat fermentation with suction / air feeding in the primary fermentor for 10 days to give moisture of 42.0%. Fermentation with repeated suction / air feeding for 7 days in the secondary fermentor The water content was 36.0%. About 90% of the amount was returned to the infiltration mixing tank, and the remaining 10% (water content 35.0%) was fermented while being sent to the tertiary fermenter (50 days) (water content 25.0%). Furthermore, fermentation and aging were carried out while staying and supplying air for 88 days in the product storage. A final product of 8.0 t / day with a moisture content of 20.0% was obtained.
実施例2により製造されたフライアッシュ発酵物(有機ケイ酸肥料)87kgに塩化カリ10kgと水酸化マグネシウム3kgとを混合撹拌機により混合して、100kgの水稲用肥料を得た。 10 kg of potassium chloride and 3 kg of magnesium hydroxide were mixed with 87 kg of fly ash fermented product (organosilicate fertilizer) produced in Example 2 using a mixing stirrer to obtain 100 kg of paddy rice fertilizer.
実施例2により製造されたフライアッシュ発酵物(有機ケイ酸肥料)を、このまま畑作物の土壌に適宜量散布した。その結果、土壌は、団粒化し、肥沃となり、有機ケイ酸肥料を散布しない畑の作物に比して、生育が良好となった。
An appropriate amount of the fly ash fermented product (organosilicate fertilizer) produced in Example 2 was sprayed on the field crop soil as it was. As a result, the soil became agglomerated and fertile, and the soil grew better than the field crops that were not sprayed with organosilicate fertilizer.
Claims (6)
A fertilizer for paddy rice, wherein the fertilizer according to any one of claims 3 to 5 is used as a fertilizer for paddy rice.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2005221794A JP2007039253A (en) | 2005-07-29 | 2005-07-29 | Organic silicate fertilizer |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2005221794A JP2007039253A (en) | 2005-07-29 | 2005-07-29 | Organic silicate fertilizer |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2007039253A true JP2007039253A (en) | 2007-02-15 |
Family
ID=37797581
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2005221794A Pending JP2007039253A (en) | 2005-07-29 | 2005-07-29 | Organic silicate fertilizer |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2007039253A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2009096647A (en) * | 2007-10-12 | 2009-05-07 | Oji Paper Co Ltd | Organic fertilizer and method of manufacturing the same |
CN102731187A (en) * | 2012-06-27 | 2012-10-17 | 吉林省农业科学院 | Liquid fertilizer used for eggplant based on biogas slurry and its application method |
CN107556132A (en) * | 2017-09-04 | 2018-01-09 | 锡林郭勒职业学院 | A kind of preparation method of fly ash base artificial soil |
CN112047778A (en) * | 2020-08-06 | 2020-12-08 | 内蒙古工业大学 | Water-retaining slow-release organic fertilizer prepared by taking active silicon material as additive and preparation method thereof |
-
2005
- 2005-07-29 JP JP2005221794A patent/JP2007039253A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2009096647A (en) * | 2007-10-12 | 2009-05-07 | Oji Paper Co Ltd | Organic fertilizer and method of manufacturing the same |
CN102731187A (en) * | 2012-06-27 | 2012-10-17 | 吉林省农业科学院 | Liquid fertilizer used for eggplant based on biogas slurry and its application method |
CN107556132A (en) * | 2017-09-04 | 2018-01-09 | 锡林郭勒职业学院 | A kind of preparation method of fly ash base artificial soil |
CN112047778A (en) * | 2020-08-06 | 2020-12-08 | 内蒙古工业大学 | Water-retaining slow-release organic fertilizer prepared by taking active silicon material as additive and preparation method thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Shan et al. | Additives for reducing nitrogen loss during composting: A review | |
CN106986720A (en) | The method for producing soil conditioner using the waste residue for handling livestock breeding wastewater generation | |
US9919976B1 (en) | Soil conditioners and method of making them | |
CN106187341B (en) | Cultivate excreta three grade fermemtation method | |
CN104016557A (en) | Governance method for realizing resource utilization and zero pollution emission of piggery wastes | |
KR20130123276A (en) | Method for treating wastewater and composting of organic wastes | |
CN103664257B (en) | Preparation method of biogas slurry cured organic fertilizer | |
CN104003773A (en) | Biological organic fertilizer and preparation method thereof | |
CN110316902A (en) | A kind of livestock and poultry feces cleaning Treatment for Reuse and resource utilization facility and implementation method | |
CN101665312A (en) | Livestock and poultry manure treating agent | |
JP5791728B2 (en) | Manufacturing method of organic fertilizer | |
CN103641593B (en) | Method for preparing garden media from biogas slurry | |
CN110357727A (en) | A kind of charcoal base organic fertilizer and its production method | |
Harrison et al. | Anaerobic digestion of dairy and swine waste | |
JP2007175048A (en) | Culture medium to be used in organic cultivation of field crop | |
Wilkie | Anaerobic digestion of flushed dairy manure | |
CN113307369A (en) | Livestock and poultry farm manure recycling and ammonia-control carbon-reduction full-chain emission reduction system and method | |
WO1994003411A1 (en) | Liquid livestock waste treating method | |
JP2007039253A (en) | Organic silicate fertilizer | |
Sajjad et al. | Methods for the removal and recovery of nitrogen and phosphorus nutrients from animal waste: A critical review | |
CN111099800A (en) | Method for recycling livestock and poultry manure | |
WO1993024418A1 (en) | Method for processing liquide manure | |
US20220186164A1 (en) | Methods and apparatuses for processing poultry litter | |
CN214299801U (en) | Combined energy-saving automatic circulation ecological system | |
KR19980076708A (en) | Fertilizer Manufacturing Process Using Sewage Sludge Sludge and Fly Ash |